Ecological Risk Assessment for Section 3 Registration for Fruit,
Vegetable, Selected Field Crop, Turf and Ornamental Uses of
Chlorantraniliprole (PC Code 090100)

(DP Barcode: DP338512)

Prepared By:

Edward Odenkirchen, Ph.D.

James Hetrick, Ph.D.

Environmental Risk Branch 1

Environmental Fate and Effects Division

Office of Pesticide Programs

Approved By:

Nancy Andrews, Ph. D., Chief

Environmental Risk Branch 1

Environmental Fate and Effects Division

Office of Pesticide Programs

  TOC \o "2-3" \h \z \t "Heading 1,1"  

  HYPERLINK \l "_Toc184543438"  I.	EXECUTIVE SUMMARY	  PAGEREF
_Toc184543438 \h  4  

  HYPERLINK \l "_Toc184543439"  A.	Nature of Stressor	  PAGEREF
_Toc184543439 \h  4  

  HYPERLINK \l "_Toc184543440"  1. 	Effects Summary	  PAGEREF
_Toc184543440 \h  4  

  HYPERLINK \l "_Toc184543441"  2.	Fate Summary	  PAGEREF _Toc184543441
\h  4  

  HYPERLINK \l "_Toc184543442"  B.	Potential Risk to Non-Target
Organisms	  PAGEREF _Toc184543442 \h  5  

  HYPERLINK \l "_Toc184543443"  1.	Terrestrial Plants	  PAGEREF
_Toc184543443 \h  5  

  HYPERLINK \l "_Toc184543444"  2.	Terrestrial Invertebrates	  PAGEREF
_Toc184543444 \h  5  

  HYPERLINK \l "_Toc184543445"  3.	Terrestrial Vertebrates	  PAGEREF
_Toc184543445 \h  6  

  HYPERLINK \l "_Toc184543446"  4.	Aquatic Plants	  PAGEREF
_Toc184543446 \h  6  

  HYPERLINK \l "_Toc184543447"  5.	Freshwater Fish and Amphibians	 
PAGEREF _Toc184543447 \h  6  

  HYPERLINK \l "_Toc184543448"  6.	Freshwater Invertebrates	  PAGEREF
_Toc184543448 \h  6  

  HYPERLINK \l "_Toc184543449"  7.	Estuarine/Marine Fish	  PAGEREF
_Toc184543449 \h  8  

  HYPERLINK \l "_Toc184543450"  8.	Estuarine/Marine Invertebrates	 
PAGEREF _Toc184543450 \h  9  

  HYPERLINK \l "_Toc184543451"  9.	Assessment of Potential Effects to
Federally Listed Threatened and Endangered Species	  PAGEREF
_Toc184543451 \h  11  

  HYPERLINK \l "_Toc184543452"  II.	PROBLEM FORMULATION	  PAGEREF
_Toc184543452 \h  12  

  HYPERLINK \l "_Toc184543453"  A.	Nature of the Federal Action	 
PAGEREF _Toc184543453 \h  12  

  HYPERLINK \l "_Toc184543454"  B.	Nature of the Chemical Stressor	 
PAGEREF _Toc184543454 \h  12  

  HYPERLINK \l "_Toc184543455"  C.	Use Characterization	  PAGEREF
_Toc184543455 \h  14  

  HYPERLINK \l "_Toc184543456"  D. 	Ecological Receptors Considered in
this Risk Assessment	  PAGEREF _Toc184543456 \h  18  

  HYPERLINK \l "_Toc184543457"  E. 	Exposure Pathways Considered for
Terrestrial Organisms	  PAGEREF _Toc184543457 \h  18  

  HYPERLINK \l "_Toc184543458"  F.	Exposure Pathways Considered for
Aquatic Organisms	  PAGEREF _Toc184543458 \h  19  

  HYPERLINK \l "_Toc184543459"  G.	Conceptual Model	  PAGEREF
_Toc184543459 \h  19  

  HYPERLINK \l "_Toc184543460"  1.	Risk Hypothesis	  PAGEREF
_Toc184543460 \h  19  

  HYPERLINK \l "_Toc184543461"  2.	Conceptual Diagram	  PAGEREF
_Toc184543461 \h  20  

  HYPERLINK \l "_Toc184543462"  H.  Analysis Plan	  PAGEREF
_Toc184543462 \h  20  

  HYPERLINK \l "_Toc184543463"  1.	Preliminary Identification of Data
Gaps and Methods	  PAGEREF _Toc184543463 \h  20  

  HYPERLINK \l "_Toc184543464"  2.	Assessment Endpoints	  PAGEREF
_Toc184543464 \h  21  

  HYPERLINK \l "_Toc184543465"  3.	Exposure Measures	  PAGEREF
_Toc184543465 \h  21  

  HYPERLINK \l "_Toc184543466"  4.	Effects Measures	  PAGEREF
_Toc184543466 \h  23  



  HYPERLINK \l "_Toc184543467"  IV. 	ANALYSIS	  PAGEREF _Toc184543467 \h
 24  

  HYPERLINK \l "_Toc184543468"  A. 	Environmental Fate and Transport
Characterization	  PAGEREF _Toc184543468 \h  24  

  HYPERLINK \l "_Toc184543469"  1.  Aquatic Organism Exposure	  PAGEREF
_Toc184543469 \h  28  

  HYPERLINK \l "_Toc184543470"  2. 	Terrestrial Vertebrate Exposure	 
PAGEREF _Toc184543470 \h  33  

  HYPERLINK \l "_Toc184543471"  3.	Terrestrial Invertebrate Exposure	 
PAGEREF _Toc184543471 \h  33  

  HYPERLINK \l "_Toc184543472"  4.	Terrestrial Plant Exposure	  PAGEREF
_Toc184543472 \h  33  

  HYPERLINK \l "_Toc184543473"  B.  	Effects Characterization	  PAGEREF
_Toc184543473 \h  34  

  HYPERLINK \l "_Toc184543474"  1.	Avian Toxicity	  PAGEREF
_Toc184543474 \h  35  

  HYPERLINK \l "_Toc184543475"  2.	Mammalian Toxicity	  PAGEREF
_Toc184543475 \h  36  

  HYPERLINK \l "_Toc184543476"  3.	Terrestrial Invertebrate Toxicity	 
PAGEREF _Toc184543476 \h  37  

  HYPERLINK \l "_Toc184543477"  4. 	Terrestrial Plant Toxicity	  PAGEREF
_Toc184543477 \h  40  

  HYPERLINK \l "_Toc184543478"  5.	Freshwater Invertebrate Toxicity	 
PAGEREF _Toc184543478 \h  41  

  HYPERLINK \l "_Toc184543479"  6.	Freshwater Fish Toxicity	  PAGEREF
_Toc184543479 \h  43  

  HYPERLINK \l "_Toc184543480"  7.	Estuarine/Marine Invertebrate
Toxicity	  PAGEREF _Toc184543480 \h  44  

  HYPERLINK \l "_Toc184543481"  8.	Estuarine Marine Fish Toxicity	 
PAGEREF _Toc184543481 \h  45  

  HYPERLINK \l "_Toc184543482"  9.	Aquatic Plant Toxicity	  PAGEREF
_Toc184543482 \h  46  

  HYPERLINK \l "_Toc184543483"  10.	Summary of Effects Measurement
Endpoint Values Used in the Risk Assessment	  PAGEREF _Toc184543483 \h 
47  

  HYPERLINK \l "_Toc184543484"  V. 	RISK CHARACTERIZATION	  PAGEREF
_Toc184543484 \h  48  

  HYPERLINK \l "_Toc184543485"  A. 	Risk Estimation	  PAGEREF
_Toc184543485 \h  48  

  HYPERLINK \l "_Toc184543486"  1.	Terrestrial Vertebrate Risk Quotients
  PAGEREF _Toc184543486 \h  48  

  HYPERLINK \l "_Toc184543487"  2.	Terrestrial Invertebrate Risk
Quotients	  PAGEREF _Toc184543487 \h  49  

  HYPERLINK \l "_Toc184543488"  3.	Terrestrial Plant Risk Quotients	 
PAGEREF _Toc184543488 \h  49  

  HYPERLINK \l "_Toc184543489"  4.	Freshwater Fish Risk Quotients	 
PAGEREF _Toc184543489 \h  50  

  HYPERLINK \l "_Toc184543490"  5.	Freshwater Invertebrate Risk
Quotients	  PAGEREF _Toc184543490 \h  52  

  HYPERLINK \l "_Toc184543491"  6.	Estuarine/Marine Fish Risk Quotients	
 PAGEREF _Toc184543491 \h  54  

  HYPERLINK \l "_Toc184543492"  7.	Estuarine/Marine Invertebrate Risk
Quotients	  PAGEREF _Toc184543492 \h  56  

  HYPERLINK \l "_Toc184543493"  8.	Aquatic Plants	  PAGEREF
_Toc184543493 \h  58  

  HYPERLINK \l "_Toc184543494"  B.	Risk Discussion	  PAGEREF
_Toc184543494 \h  62  

  HYPERLINK \l "_Toc184543495"  1.	Quantified Risks	  PAGEREF
_Toc184543495 \h  62  

  HYPERLINK \l "_Toc184543496"  2.	Qualitative Discussion of Terrestrial
Plant Risks	  PAGEREF _Toc184543496 \h  67  

  HYPERLINK \l "_Toc184543497"  3.	Qualitative Discussion of Terrestrial
Invertebrate Risks	  PAGEREF _Toc184543497 \h  67  

  HYPERLINK \l "_Toc184543498"  VI. 	FEDERALLY LISTED THREATENED AND
ENDANGERED SPECIES ASSESSMENT	  PAGEREF _Toc184543498 \h  68  

  HYPERLINK \l "_Toc184543499"  A.  	Action Area	  PAGEREF _Toc184543499
\h  68  

  HYPERLINK \l "_Toc184543500"  B.	Taxonomic Groups Potentially at Risk	
 PAGEREF _Toc184543500 \h  69  

  HYPERLINK \l "_Toc184543501"  C.	Analysis of Dose Response (Effects
Study Slope)	  PAGEREF _Toc184543501 \h  70  

  HYPERLINK \l "_Toc184543502"  D.	Consideration of Alternative
Assumptions of Drift.  (Need to Work ON)	  PAGEREF _Toc184543502 \h  71 


  HYPERLINK \l "_Toc184543503"  E.	Critical Habitat	  PAGEREF
_Toc184543503 \h  72  

  HYPERLINK \l "_Toc184543504"  F.	Co-Location Analysis	  PAGEREF
_Toc184543504 \h  73  

 

I.	EXECUTIVE SUMMARY

A.	Nature of Stressor

The subject of this risk assessment is a Federal Insecticide, Fungicide,
Rodenticide Act (FIFRA) Section 3 registration for the use of the
insecticide chlorantraniliprole.  This insecticide is proposed for a
variety of use sites including brassica (cole), leafy vegetables
(broccoli, broccoli raab, brussels sprouts, cabbage, chinese cabbage,
cauliflower, cavalo broccoli, collards, kale, kohlrabi, mizuna, mustard
greens, mustard spinach, rape greens), curcurbits (vegetables, melons,
squash), and fruiting vegetables (eggplant, goundcherry, peppers,
tomatoes),  non-brassica leafy vegetables (celery, lettuce, spinach,
Arugula, Cardoon, Amaranth leafy),  cotton, grape, pome fruit (apple,
crabapple, loquat, mayhaw, pear, oriental pear, and quice), potato,
stone fruits (apricot, sweet cherry, tart cherry, plum, chickasaw plum,
Damson plum, Japanese plum, plumcot, prune),  turf,  ornamental plants,
and groundcovers.  

1. 	Effects Summary

There were no data gaps in the effects data.    In agreement with
international governmental partners associated with registration efforts
for this pesticide, ecological effects data evaluation responsibilities
are being met through the efforts of the Pesticides Safety Directorate
(PSD), UK.  The Agency is using the results of the PSD review as they
appear in the dossier for registration in Europe.  Except where
specifically reported, independent validation of statistical results for
effects studies was not performed during the PSD reviews.

Chlorantraniliprole can be characterized as having very little toxicity
to terrestrial and aquatic vertebrates.  As can be expected for an
insecticide, the compound is toxic to a number of terrestrial and
aquatic invertebrates.  The compound can produce limited adverse effects
in terrestrial and aquatic plants. 

Available data for formulated products suggested no concern for enhanced
toxicity of formulations versus the active ingredient alone.  Data for
degradates suggest no concern for toxicity exceeding the parent compound
and in most cases toxicity is orders of magnitude below the parent.  

2.	Fate Summary

There were no identified data gaps in the fate data.  Under
international agreements the Agency was not responsible for conducting
environmental fate data reviews.  Data review is being conducted for use
by all parties to the international agreement by the Pesticide Control
Service, Department of Agriculture and Food, Ireland. The Agency is
using the results of the PSD review as they appear in the dossier for
registration in Europe except for the aerobic soil metabolism
half-lives.  EFED recalculated aerobic soil metabolism half-lives for
chlorantraniliprole to be representative of the total extractable
chlorantraniliprole fraction in soil.  The total extractable soil
fraction of chlorantraniliprole (water pre-soak and acetonitrile/water +
acid/surfactants or concentrated acid at evaluated temperature) was used
to a conservative half-life of bioavailable chlorantraniliprole in soil.
   

Based on this review, chlorantraniliprole may be characterized as
persistent and mobile in terrestrial and aquatic environments. Extended
chlorantraniliprole use is expected to cause accumulation of residues in
soil from year to year.  Major routes of dissipation are expected to be
alkaline-catalyzed hydrolysis, photodegradation in water, leaching, and
runoff.

Nine degradates/metabolites of the parent compound have been identified
in environmental fate studies: IN-EQW78, IN-LBA22, IN-LBA24, IN-LBA23

IN-ECD73, IN-F6L99, IN-EVK64, IN-F9N04, and IN-GAZ70.  The greatest
percentage production of a degradate was for IN-LBA24, which was 90% of
applied parent produced in the photolysis study at pH7.   This risk
assessment did not quantify the risks from these degradates because they
were commonly of lower toxic potency than the parent. For example
IN-LBA24 is orders of magnitude less toxic than the parent pesticide. 
Coupling the observed lower toxic potency with the risk assessments
exposure modeling assumptions of stability for the parent would suggest
that excluding the degradates from quantitative risk estimation would
not substantially affect the conclusion of the risk assessment.

B.	Potential Risk to Non-Target Organisms

1.	Terrestrial Plants

The conclusion of the risk assessment is that best available information
indicates that risks of direct effects to non-listed terrestrial plants
are below Agency screening levels of concern.

2.	Terrestrial Invertebrates

While the Agency currently does not use a standard method for
quantifying risks of pesticides to terrestrial invertebrates, available
effects data for insect species, when compared with application rates
suggest that the insecticide chlorantraniliprole has the potential to
produce direct adverse effects in some non-target insect species.  It
appears from the effects data that sensitivity to the pesticide is quite
varied among tested invertebrates.  If species specific risk assessment
becomes necessary (e.g., assessment of a federally listed threatened or
endangered species) it is recommended that closer evaluation of the
potential representation of the invertebrate data set for a specific
organism be considered.

3.	Terrestrial Vertebrates

The conclusion of the risk assessment is that best available information
indicates that risks of direct effects to non-listed terrestrial
vertebrates are below Agency screening levels of concern.

4.	Aquatic Plants

The conclusion of the risk assessment is that best available information
indicates that risks of direct effects to non-listed aquatic plants are
below Agency screening levels of concern.

5.	Freshwater Fish and Amphibians

The conclusion of the risk assessment is that best available information
indicates that risks of direct effects to non-listed freshwater fish and
amphibians are below Agency screening levels of concern.

6.	Freshwater Invertebrates

The following tables present the conclusions of the risk assessment for
freshwater invertebrates.  Acute concerns are triggered by freshwater
invertebrate RQ values for every exposure scenario modeled (except for
ground spray for the OR apple and CA turf scenarios, which involve lower
rainfall assumptions and thus lower estimates of aquatic exposure).
These concerns are limited primarily to acute effects to listed species
and restricted use considerations.

Chronic freshwater invertebrate risk concerns were identified for
proposed uses on  FL peppers (ground or aerial spray), FL cucumbers
(ground or aerial spray), CA nursery (ground spray), FL nursery (ground
spray), and TN nursery (ground spray).  In all cases the RQs were less
than an order of magnitude above the Agency concern level.  These
chronic endpoints are calculated using the most sensitive chronic NOEC
for daphnids (4.47 ug/L ug/L). 

 

Tier II RQs  for FW Invertebrates from Aerial Spray Application  of
DPX-E2Y45 for Various Crop Types 

Scenario	Application	Peak	

21-day

Average	Acute1 RQ	Chronic2

RQ	Identified

Concerns

	Rate

(lbs/A)	#	Int

(days)





	FL cabbage	0.065	3	3	2.652	2.146	0.1850	0.4801	RU,LS

FL cucumber	0.065	3	5	5.693	4.939	0.4258	1.1049	RU,LS, Chronic

PA tomato	0.098	2	5	1.513	1.306	0.1126	0.2922	RU,LS

CA tomato	0.098	2	5	1.080	0.922	0.0795	0.2063	LS

FL tomato	0.098	2	5	3.660	3.001	0.2587	0.6714	RU,LS

FL peppers	0.098	2	5	6.749	5.683	0.4899	1.2714	RU,LS Chronic

CA lettuce	0.065	3	3	3.579	2.997	0.2584	0.6705	RU,LS

CA cotton	0.099	2	5	1.785	1.576	0.1359	0.3526	RU,LS

NC cotton	0.099	2	5	3.730	3.207	0.2765	0.7174	RU,LS

MS cotton	0.099	2	5	3.769	3.271	0.2820	0.7318	RU,LS

NY grape	0.099	2	7	1.389	1.197	0.1032	0.2678	RU,LS

CA grape	0.099	2	7	1.188	1.026	0.0884	0.2295	LS

NC apple	0.099	2	10	1.359	1.153	0.0994	0.2579	LS

PA apple	0.099	2	10	1.245	1.091	0.0941	0.2441	LS

OR apple	0.099	2	10	0.786	0.674	0.0581	0.1508	LS

ID potato	0.066	3	5	1.021	0.859	0.0741	0.1922	LS

ME potato	0.066	3	5	1.558	1.392	0.1200	0.3114	RU,LS

GA peach	0.099	2	7	1.086	0.886	0.0764	0.1982	LS

MI Cherry	0.099	2	7	1.035	0.907	0.0782	0.2029	LS

1-Acute Toxicity Endpoint= 11.6 µg/L

2-Chronic Toxicity Endpoint= 4.47 µg/L 

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5),
restricted use (0.1), and listed species (0.05).  Chronic RQs compared
with chronic LOC of 1.



Tier II RQs  for FW Invertebrates from Ground Spray Application  of
DPX-E2Y45 for Various Crop Types 

Scenario	Application	

Peak	

21-day

Average	Acute1 RQ	Chronic2

RQ	Identified

Concerns

	Rate

(lbs/A)	#	Int





	FL cabbage	0.065	3	3	2.531	2.045	0.1763	0.4575	RU,LS

FL cucumber	0.065	3	5	5.624	4.86	0.4190	1.0872	RU,LS, Chronic 

PA tomato	0.098	2	5	1.280	1.097	0.0946	0.2454	LS

CA tomato	0.098	2	5	0.731	0.619	0.0534	0.1385	LS

FL tomato	0.098	2	5	3.436	2.817	0.2428	0.6302	RU,LS

FL peppers	0.098	2	5	6.501	5.475	0.4720	1.2248	RU,LS, Chronic

CA lettuce	0.065	3	3	3.311	2.781	0.2397	0.6221	RU,LS

CA cotton	0.099	2	5	1.470	1.28	0.1103	0.2864	RU,LS

NC cotton	0.099	2	5	3.473	2.995	0.2582	0.6700	RU,LS

MS cotton	0.099	2	5	3.575	3.116	0.2686	0.6971	RU,LS

NY grape	0.099	2	7	1.189	1.025	0.0884	0.2293	LS

CA grape	0.099	2	7	0.813	0.706	0.0609	0.1579	LS

NC apple	0.099	2	10	0.999	0.852	0.0734	0.1906	LS

PA apple	0.099	2	10	1.048	0.898	0.0774	0.2009	LS

OR apple	0.099	2	10	0.410	0.365	0.0315	0.0817	None

ID potato	0.066	3	5	0.812	0.68	0.0586	0.1521	LS

ME potato	0.066	3	5	1.350	1.195	0.1030	0.2673	RU,LS

GA peach	0.099	2	7	0.763	0.62	0.0534	0.1387	LS

MI Cherry	0.099	2	7	0.867	0.739	0.0637	0.1653	LS

FLTurf	0.26	2	7	0.837	0.707	0.0609	0.1582	LS

PA Turf	0.26	2	7	1.102	0.985	0.0849	0.2204	LS

CA Turf	0.26	2	7	0.654	0.554	0.0478	0.1239	None

CA Nursery	0.4992	1	NA	5.663	4.672	0.4028	1.0452	RU,LS, Chronic

CA Residential	0.4992	1	NA	1.779	1.543	0.1330	0.3452	RU,LS

FL Nursery	0.4992	1	NA	9.785	8.136	0.7014	1.8201	RU,LS, Chronic

MI Nursery	0.4992	1	NA	2.508	2.284	0.1969	0.5110	RU,LS

TN Nursery	0.4992	1	NA	10.981	9.126	0.7867	2.0416	RU,LS, Chronic

1-Acute Toxicity Endpoint=11.6 µg/L

2-Chronic Toxicity Endpoint= 4.47 µg/L 

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5),
restricted use (0.1), and listed species (0.05).  Chronic RQs compared
with chronic LOC of 1.

7.	Estuarine/Marine Fish

The conclusion of the risk assessment is that best available information
indicates risks of direct effects to non-listed estuarine/marine fish
are below Agency screening levels of concern.



8.	Estuarine/Marine Invertebrates

The following table summarizes the proposed use sites associated with
each model scenario and identifies the Agency concern levels exceeded. 
Risks to estuarine/marine invertebrates that exceed Agency concern
levels are confined to the following Tier II modeling scenarios: FL
cabbage (aerial or ground spray), FL cucumber (aerial or ground spray),
FL peppers (aerial or ground spray), FL tomatoes (aerial spray),  CA
lettuce (ground and aerial spray), NC cotton (aerial or ground spray),
MS cotton (aerial or ground spray) CA nursery (ground spray), TN nursery
(ground spray), FL nursery (ground spray), and MI nursery (ground
spray).  These risks are generally limited to acute effects to listed
species. However, the restricted use LOCs  are exceeded for the Florida
vegetable scenarios (cucumber, peppers) and nursery use scenarios (CA
nursery, TN nursery, and FL nursery scenarios).   

Tier II RQs  for Estuarine/Marine Invertebrates from Aerial Spray
Application  of DPX-E2Y45 for Various Crop Types 

Scenario	Application	

Peak	

21-day

Average	Acute1 RQ	Chronic2

RQ	Identified

Concerns

	Rate

(lbs/A)	#	Int





	FL cabbage	0.065	3	3	2.652	2.146	0.0538	0.0894	LS

FL cucumber	0.065	3	5	5.693	4.939	0.1238	0.2058	RU,LS

PA tomato	0.098	2	5	1.513	1.306	0.0327	0.0544	None

CA tomato	0.098	2	5	1.080	0.922	0.0231	0.0384	None

FL tomato	0.098	2	5	3.660	3.001	0.0752	0.1250	LS

FL peppers	0.098	2	5	6.749	5.683	0.1424	0.2368	RU,LS

CA lettuce	0.065	3	3	3.579	2.997	0.0751	0.1249	LS

CA cotton	0.099	2	5	1.785	1.576	0.0395	0.0657	None

NC cotton	0.099	2	5	3.730	3.207	0.0804	0.1336	LS

MS cotton	0.099	2	5	3.769	3.271	0.0820	0.1363	LS

NY grape	0.099	2	7	1.389	1.197	0.0300	0.0499	None

CA grape	0.099	2	7	1.188	1.026	0.0257	0.0428	None

NC apple	0.099	2	10	1.359	1.153	0.0289	0.0480	None

PA apple	0.099	2	10	1.245	1.091	0.0273	0.0455	None

OR apple	0.099	2	10	0.786	0.674	0.0169	0.0281	None

ID potato	0.066	3	5	1.021	0.859	0.0215	0.0358	None

ME potato	0.066	3	5	1.558	1.392	0.0349	0.0580	None

GA peach	0.099	2	7	1.086	0.886	0.0222	0.0369	None

MI Cherry	0.099	2	7	1.035	0.907	0.0227	0.0378	None

1-Acute Toxicity Endpoint= 39.9 µg/L

2-Chronic Toxicity Endpoint= 24 µg/L 

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5),
restricted use (0.1), and listed species (0.05).  Chronic RQs compared
with chronic LOC of 1.



Tier II RQs  for Estuarine/Marine Invertebrates from Ground Spray
Application  of DPX-E2Y45 for Various Crop Types 

Scenario	Application	

Peak	

21-day

Average	Acute1 RQ	Chronic2

RQ	Identified

Concerns

	Rate

(lb/A)	#	Int





	FL cabbage	0.065	3	3	2.531	2.045	0.0513	0.0852	LS

FL cucumber	0.065	3	5	5.624	4.86	0.1218	0.2025	RU,LS

PA tomato	0.098	2	5	1.280	1.097	0.0275	0.0457	None

CA tomato	0.098	2	5	0.731	0.619	0.0155	0.0258	None

FL tomato	0.098	2	5	3.436	2.817	0.0706	0.1174	None

FL peppers	0.098	2	5	6.501	5.475	0.1372	0.2281	RU,LS

CA lettuce	0.065	3	3	3.311	2.781	0.0697	0.1159	LS

CA cotton	0.099	2	5	1.470	1.28	0.0321	0.0533	None

NC cotton	0.099	2	5	3.473	2.995	0.0751	0.1248	LS

MS cotton	0.099	2	5	3.575	3.116	0.0781	0.1298	LS

NY grape	0.099	2	7	1.189	1.025	0.0257	0.0427	None

CA grape	0.099	2	7	0.813	0.706	0.0177	0.0294	None

NC apple	0.099	2	10	0.999	0.852	0.0214	0.0355	None

PA apple	0.099	2	10	1.048	0.898	0.0225	0.0374	None

OR apple	0.099	2	10	0.410	0.365	0.0091	0.0152	None

ID potato	0.066	3	5	0.812	0.68	0.0170	0.0283	None

ME potato	0.066	3	5	1.350	1.195	0.0299	0.0498	None

GA peach	0.099	2	7	0.763	0.62	0.0155	0.0258	None

MI Cherry	0.099	2	7	0.867	0.739	0.0185	0.0308	None

FLTurf	0.26	2	7	0.837	0.707	0.0177	0.0295	None

PA Turf	0.26	2	7	1.102	0.985	0.0247	0.0410	None

CA Turf	0.26	2	7	0.654	0.554	0.0139	0.0231	None

CA Nursery	0.4992	1	NA	5.663	4.672	0.1171	0.1947	RU,LS

CA Residential	0.4992	1	NA	1.779	1.543	0.0387	0.0643	None

FL Nursery	0.4992	1	NA	9.785	8.136	0.2039	0.3390	RU,LS

MI Nursery	0.4992	1	NA	2.508	2.284	0.0572	0.0952	LS

TN Nursery	0.4992	1	NA	10.981	9.126	0.2287	0.3803	RU,LS

1-Acute Toxicity Endpoint=39.9 µg/L

2-Chronic Toxicity Endpoint= 24 µg/L 

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5),
restricted use (0.1), and listed species (0.05).  Chronic RQs compared
with chronic LOC of 1.



9.	Assessment of Potential Effects to Federally Listed Threatened and
Endangered Species

The following table summarizes the conclusions of potential concerns for
direct and indirect effects to federally-listed threatened and
endangered species (listed species).

Potential Effects to Federally Listed Taxa





Listed Taxa	Direct Effects	Scenario Identified as of Concern	Indirect
Effects	Scenario Identified as of Concern

Terrestrial and semi-aquatic plants - monocots	Yes4

Yes1	all

Terrestrial and semi-aquatic plants - dicots	Yes4

Yes1	all

Terrestrial invertebrates	Yes	all	No

	Birds	No

Yes1,2,3,5	All 

Terrestrial phase amphibians	No

Yes1,2,5	All 

Reptiles	No

Yes1,2,3,5	All 

Mammals	No

Yes1,2,3,5	All 

Aquatic vascular plants	No

No

	Freshwater fish	No

Yes2,5	All 

Aquatic phase amphibians	No

Yes2,5	All 

Freshwater crustaceans	Yes	All except  CA turf (ground spray) and OR
apple (ground spray)	Yes2,5	All

Mollusks	Yes(may be subject to further evaluation)	All except  CA turf
(ground spray) and OR apple (ground spray)	Yes2,5	All

Marine/estuarine fish	No

Yes3	FL cabbage, FL cucumber, FL pepper, NC cotton, MS cotton,  CA
lettuce, CA nursery, FL nursery, MI nursery, TN nursery



Marine/estuarine invertebrates	Yes	FL cabbage, FL cucumber, FL pepper,
NC cotton, MS cotton,  CA lettuce, CA nursery, FL nursery, MI nursery,
TN nursery

	No

	1 direct effects on terrestrial invertebrates

2 direct effects on aquatic invertebrates

3 direct effects on estuarine/marine invertebrates

4 insufficient data to preclude risk

5direct effects to terrestrial plants at the listed species level of
concern suggests concern of animals with obligate relationships to a
plant species



II.	PROBLEM FORMULATION

A.	Nature of the Federal Action

DuPont crop protection is requesting an Agency decision regarding a
FIFRA Section 3 registration for the pesticide chlorantraniliprole.  The
nature of the uses of the pesticide under this proposed EUP is discussed
in the Use Characterization section of this risk assessment.

B.	Nature of the Chemical Stressor

The risk assessment addresses the active ingredient chlorantraniliprole.
 The following information summarizes basic chemical identity
information for the active ingredient:

	Chemical Name: 3-Bromo-N-[4-chloro-2-methyl-6- [(methylamino) 
carbonyl]phenyl]-1-(3-chloro-2-pyridinyl)-1H-pyrazole-5-carboxamide

	Empirical Formula: C18H14N5O2BrCl2

	Molecular Weight: 483.15 g/mole

	CAS No.: 500008-45-7 (chlorantraniliprole)

	Common Name: chlorantraniliprole

	Pesticide Type: Insecticide

	Chemical Family: Anthranilic diamide

	Physical State: Fine Crystalline Powder

	Odor: No odor

	pH: 5.77 ± 0.087 at 20oC

UV/Visible Absorption: A lambda max under basic conditions was ~320 nm.
No defined lambda max, 	above 290 nm, under neutral or acidic
conditions.

	Melting Point: 208-210oC

	Relative Density: 1.5070 at 20oC

	Dissociation Constant in Water: pKa was approximately 10.88 ± 0.71 at
20°C

	Partition Coefficient: Kow (20°C ) = 2.77 at pH 4, 2.86 at pH7 & 2.80
at pH9

Water Solubility: pH 4: 0.972 mg/L (CV = 1.9%) pH 7: 0.880 mg/L (CV =
1.3%) pH 9: 	0.971 mg/L (CV = 3.8%)

	Solubility in Organic Solvents at 20oC:

	Acetone 3.446 g/l

	Acetonitrile 0.711g/l

	Ethyl acetate 1.144 g/l

	Dichloromethane 2.476 g/l

	Dimethylformamide 2.476 g/l

	1-Octanol 0.386 g/l

	Methanol 1.714 g/l

	n-Hexane <0.0001 g/l

	o-Xylene 0.162 g/l

	Vapor Pressure (est.): 6.3 x 10-12 PA at20oC (2.1 x 10-11Pa at 25oC)

	Henry’s Law Constant: 3.1 x 10-15 atm-m3/mol (20oC) (3.1 x 10-10
Pa-m3/mol)

The structure of the active ingredient is reported as follows:

While degradates have been identified, the available effects data
indicate that their toxicity is lower than the parent, often by an order
of magnitude.  The greatest percentage production of a degradate was for
IN-LBA24, which was 90% of applied parent produced in the
photodegradation study at a buffered pH of  7.  Even at this maximum
production of degradate, the low toxicity (one tenth that of parent)
would not affect quantitative risk estimations to any significant
degree, and it was assumed that further quantitative consideration of
risks associated with degradates would not materially add to the
confidence of the risk assessment conclusions. 

C.	Use Characterization 

The following is as list of proposed crop uses:  brassica (cole), leafy
vegetables (broccoli, broccoli raab, Brussels sprouts, cabbage, Chinese
cabbage, cauliflower, cavalo broccoli, collards, kale, kohlrabi, mizuna,
mustard greens, mustard spinach, rape greens), curcurbits (vegetables,
melons, squash), fruiting vegetables (eggplant, goundcherry, peppers,
tomatoes), cotton, grape, pome fruits, potato, and stone fruits.   The
pesticide may also be applied to turf, and ornamental plants 

Chlorantraniliprole  is proposed for the control of a variety of insect
pests on crops including beet armyworm, cotton bollworm, diamondback
moth, cabbage looper, corn earworm, cross-striped cabbageworm, imported
cabbage worm, melon worm, pickle worm, leaf miners, whiteflies
(suppression only), hornworm, southern armyworm, salt marsh caterpillar,
soybean looper, western yellow-striped armyworm, tomato fruit worm,
European corn borer, garden webworm, tomato pinworm, grape berry moth,
grape leaf roller, western grape skeletonizer, green fruit worm, spotted
tentiform leafminer, codling moth, oriental fruit moth, tufted apple cut
moth, white apple leafhopper, Colorado potato beetle, obliquebanded
leafroller, peach twig borer, and southern armyworm. In addition to crop
pests, chlorantraniliprole is proposed for control turf and ornamental
plants pests including: armyworms, sod webworms, white grubs, European
crane fly, billbugs, annual bluegrass weevil, spittle bugs, chinch bugs,
bagworms, tussock moths, lace bugs, aphids, birch leafminer, and
clearwing borers.

Proposed label application rates are presented in the following tables. 
They are influenced by product, application method (drip chemigation vs.
foliar application), crop, and target pest. 

Proposed Labeled Use Rates for CoragenTM SC



Use Site	Application Method	Target Pest	Application rate

(lb a.i./acre)	Number of Applications/ Interval

Brassica and leafy vegetables	drip chemigation	beet armyworm diamondback
moth	0.045-0.065	2 to 3 for maximum crop application of 0.2 lb a.i./acre

10 day interval 



cabbage looper, corn earworm, cross-striped cabbage worm, imported
cabbageworm	0.045-0.098



foliar (air or ground spray)	diamondback moth	0.026-0.045	4 to 7 for
maximum crop application of 0.2 lb a.i./acre

5 day interval



beet armyworm, cabbage looper, corn earworm, cross-striped cabbage worm,
imported cabbageworm	0.045-0.065	3 to 4 for maximum crop application of
0.2 lb a.i./acre

5 day interval

Cucurbits vegetables , melons, squash	drip chemigation	melon worm
0.026-0.045	4 to 7 for maximum crop application of 0.2 lb a.i./acre

10 day interval



beet armyworm, cabbage looper, pickle worm	0.045-0.065	3 to 4 for
maximum crop application of 0.2 lb a.i./acre

10 day interval



leafminers, whiteflies	0.065-0.098	2 to 3 for maximum crop application
of 0.2 lb a.i./acre

10 day interval

	foliar (air or ground spray)	melon worm	0.026-0.045	4 to 7 for maximum
crop application of 0.2 lb a.i./acre

5 day interval



beet armyworm, cabbage looper, pickle worm	0.045-0.065	3 to 4 for
maximum crop application of 0.2 lb a.i./acre

5 day interval



leafminers, whiteflies	0.065-0.09	2 to 3 for maximum crop application of
0.2 lb a.i./acre

5 day interval

Fruiting vegetables, peppers, tomatoes	drip chemigation	beet armyworm,
hornworms, southern armyworm, western yellow striped armyworm
0.045-0.065	3 to 4  for maximum crop application of 0.2 lb a.i./acre

10 day interval



tomato fruitworm, loopers	0.045-0.09	2 to 4 for maximum crop application
of 0.2 lb a.i./acre

10 day interval



european corn borer, garden webworm, leafminers, tomato pinworm,
whiteflies	0.065-0.098	2 to 3 for maximum crop application of 0.2 lb
a.i./acre

10 day interval

	foliar (air or ground spray)	hornworms	0.026-0.065	3 to 7 for maximum
crop application of 0.2 lb a.i./acre

5 day interval



beet armyworm, european corn borer, garden webworm, loopers, southern
armyworm, tomato fruitworm, tomato pinworm, western yelowstriped
armyworm	0.045-0.065	3 to 4 for maximum crop application of 0.2 lb
a.i./acre

5 day interval



leafminers, whiteflies	0.065-0.098	2 to 3 for maximum crop application
of 0.2 lb a.i./acre

5 day interval





Proposed Labeled Use Rates for AltacorTM WG



Use Site	Target Pest	Application rate

(lb a.i./acre)	Number of Applications/ Interval

Cotton	beet armyworm, cotton bollworm, fall armyworm, saltmarsh
caterpillar, southern armyworm, tobacco budworm	0.044-0.088	2 to 4
applications/season for maximum crop application of 0.2 lbs a.i./acre

5 day interval

	cabbage looper, soybean looper

	0.066-0.099

	2 to 3 applications/season for maximum crop application of 0.2 lbs
a.i./acre

5 day interval

Grape	grape berry moth, grape leafroller	0.044-0.099	No more than 4
(2-4) applications/season no more than 0.2 lbs a.i./acre

7 day interval

	omnivorous leafroller, western grapeleaf skeletonizer	0.066-0.099	No
more than 4  (2-3) applications/season no more than 0.2 lbs a.i./acre

7 day interval

Pome fruits	green fruitworm, spotted tentiform leafminer	0.044-0.088	2
to 3 applications/season for maximum crop application of 0.2 lbs
a.i./acre

10 day interval

	codling moth, obliquebanded leafroller, oriental fruit moth, tufted
apple bud moth, white apple bud moth	0.066-0.099	2 t o 3 for maximum
crop application of 0.2 lb a.i./acre

10 day interval

Potato	cabbage looper, Colorado potato beetle, European corn borer
0.044-0.066	3 to 4 applications/season for maximum crop application of
0.2 lbs a.i./acre

5 day interval



Stone fruits	Codling moth, obliquebanded leafroller, oriental fruit
moth, peach twig borer, tufted apple bud moth	0.044-0.099	No more than 4
(3-4) applications/season no more than 0.2 lbs a.i./acre

7 day interval





Proposed Labeled Use Rates for E2Y45 SC



Use Site	Application Method	Target Pest	Application rate

(lb a.i./acre)	Number of Applications/ Interval

Turf (lawns, golf courses, and other recreational turfgrass areas

	Ground spray	lepidoptera	0.026-0.052	9 to 19 

maximum annual application of 0.5 lbs a.i./acre

no interval specified



white grubs, european crane fly, 

	0.104-0.208

	2 to 4

maximum annual application of 0.5 lbs a.i./acre

no interval specified



billbugs, cinch bugs	0.104-0.26	1-4

maximum annual application of 0.5 lbs a.i./acre

no interval specified



annual bluegrass weevil, spittlebugs	0.157-0.26	1-3

maximum annual application of 0.5 lbs a.i./acre

no interval specified

Ornamental plants

	foliar spray	Leaf-feeding caterpillars	0.4992	Application numbers
specified “as needed” with 5-day intervals  However, maximum annul 
application of 0.5 lbs a.i./acre would suggest only 1 application
allowable

	soil treatment (drench or soil injection)

bark treatment	Lace bugs, aphids, birch leaf miner

clearwinged borers	Unspecified in accessible units	Application numbers
specified “as needed” with 5-day intervals  However, maximum annual
application of 0.5 lbs a.i./acre

Ornamental flowers and ground cover	soil treatment	White grubs
0.104-0.208	2 to 4 applications/year for maximum annual application of
0.5 lbs a.i./acre

5 day interval



Stone fruits

Codling moth, obliquebanded leafroller, oriental fruit moth, peach twig
borer, tufted apple bud moth	0.044-0.099	No more than 4 (2-4)
applications/season no more than 0.2 lbs a.i./acre

7 day interval



	

D. 	Ecological Receptors Considered in this Risk Assessment  TC "C.
Ecological Receptors Considered in this Risk Assessment" \f C \l "2"  

The screening level risk assessment approaches the analysis for adverse
effects commonly through the use of broad plant and animal taxonomic
groups including:

•	Birds (also used as surrogate for terrestrial-phase amphibians and
reptiles),

•	Mammals,

•	Terrestrial plants,

•	Freshwater fish (also used as a surrogate for aquatic phase
amphibians),

•	Freshwater invertebrates (including sediment-dwelling species),

Estuarine/Marine Fish

Estuarine/Marine Invertebrates

•	Algae and vascular aquatic plants

Because of known effects of chlorantraniliprole to arthropods pests, the
risks of the insecticide to non-target terrestrial invertebrates will
also be evaluated, but without the benefit of Agency established concern
thresholds to aid in interpretation of assessment results.

E. 	Exposure Pathways Considered for Terrestrial Organisms

For the purposes of this risk assessment, terrestrial non-target
organisms are assumed to occupy areas immediately adjacent to treatment
sites.   The exposure pathways analyzed in this risk assessment for
terrestrial vertebrate wildlife include dietary uptake of food items
directly treated with the pesticide at the time of application to the
treated field.  Exposures are calculated on a dietary basis alone. 
Dose-based exposures are not considered due to no evidence of acute oral
toxicity.  Accumulation from soil to plants or animal food sources is
not considered in this risk assessment.  The very low octanol/water
partitioning coefficient (log Kow =2.90) suggests that bioaccumulation
is not likely.  Inhalation of vapor phase pesticide is not considered
quantitatively in this risk assessment.  The low vapor pressure of the
parent compound (6.3 x 10-12 PA) suggests that the pesticide does not
readily volatilize and the rat acute inhalation LC50: >5.1 mg/L suggests
that what little material that would volatilize would not be of
significant toxicity.  Dermal exposure (contact with deposited residues
and impingement of spray droplets) for terrestrial vertebrates is not
considered quantitatively.  The low octanol/water partitioning
coefficient would suggest little potential to cross the dermal barrier,
a conclusion supported by the demonstrated low dermal acute toxicity in
the rat (LD50: >5000 mg/kg).  

Other routes of exposure for terrestrial wildlife that are possible but
not considered in this risk assessment include drinking water exposure,
inhalation of pesticide associated with suspended soil particulate,
inhalation of spray droplets, and oral ingestion of soil particles
through incidental contact while feeding and preening.

Terrestrial plant exposures considered potentially complete for this
pesticide include exposure of vegetation adjacent to treatment sites via
drift, sheet flow runoff, and runoff to drainage channels.  Drift
exposures are considered important to effects measures involving direct
application to leaf surfaces (e.g. vegetative vigor studies).  Drift and
runoff exposures are also comparable to effects endpoints associated
with application of pesticide to soil (e.g. seedling emergence studies).

F.	Exposure Pathways Considered for Aquatic Organisms  TC "E. Exposure
Pathways Considered for Aquatic Organisms" \f C \l "2"  

For the purposes of this risk assessment aquatic non-target organisms
are assumed to occupy a surface water body immediately adjacent to
treatment sites.   The likely pathways for introduction of the chemical
stressor to this aquatic water body include:

direct deposition of applied product through spray drift

mass transport of chemical stressor dissolved in run-off from the
treated field, and

mass transport of chemical stressor adsorbed to eroded solids from the
treated field.

Once pesticide enters the receiving waters, exposure it likely most
significant through absorption of dissolved pesticide from the water
column or interstitial water across the gill, integument, and perhaps
the gut of the organism.  Food chain exposures are not considered to be
significant for this pesticide because chlorantraniliprole has a low
fish bioconcentration factor of <21.

G.	Conceptual Model

1.	Risk Hypothesis 

The risk hypothesis for this screening-level risk assessment is as
follows:

Chlorantraniliprole, used in accordance with the Section 3 labels,
results in adverse effects upon survival and reproduction of non-target
terrestrial and aquatic organisms.  



2.	Conceptual Diagram 

The following is a conceptual plan diagram depicting sources of
exposure, potential receptors and adverse effects proposed uses of
chlorantraniliprole

H. 	Analysis Plan

H.  Analysis Plan

1.	Preliminary Identification of Data Gaps and Methods

a.	Fate Testing

There were no identified data gaps in the fate data.  Under
international agreements the Agency was not responsible for conducting
environmental fate data reviews.  Data review is being conducted for use
by all parties to the international agreement by the Pesticide Control
Service, Department of Agriculture and Food, Ireland. The Agency is
using the results of the PSD review as they appear in the dossier for
registration in Europe except for the aerobic soil metabolism
half-lives.  EFED recalculated aerobic soil metabolism half-lives for
chlorantraniliprole to be representative of the total extractable
fraction in soil. 

b.	Effects Testing

There were no data gaps in the effects data.    In agreement with
international governmental partners associated with registration efforts
for this pesticide, ecological effects data evaluation responsibilities
are being met through the efforts of the Pesticides Safety Directorate
(PSD), UK.  The Agency is using the results of the PSD review as they
appear in the dossier for registration in Europe.  Except where
specifically reported, independent validation of statistical results for
effects studies was not performed during the PSD reviews. 

2.	Assessment Endpoints

 

Assessment endpoints for this screening-level ecological risk assessment
are reduced survival, reproduction output, and growth of individual
organisms. These assessment endpoints, while measured at the individual
level, provide insight about risks at higher levels of biological
organization (e.g., populations).  It is assumed that toxicants do not
affect populations or communities except through the impact on the
individuals comprising the population or community and the demographics
of birth, growth, and death that govern population dynamics.  The number
of individuals within a population change (intrinsic rate of increase)
primarily because of births (fecundity) and deaths (survival) and
secondarily from migration in and out of a specific area.   If effects
on the survival and reproduction of individuals are limited, it is
assumed that risks at the population level from such effects will be of
minor consequence. However, as the risk of reductions in survival and/or
reproduction rates increases, so does the potential risk to populations.

3.	Exposure Measures

Exposures estimated in the screening-level risk assessment for
non-target organisms are not species specific.

For estimating exposures of aquatic organisms to chlorantraniliprole,
the risk assessment will use the PRZM/EXAMS modeling shell (PE5V01). 
Inputs for this model are presented in the Environmental Fate and
Transport Characterization section of this risk assessment. The
screening risk assessment commonly uses estimates of the dissolved
concentration of the pesticide over a single day, 21-day, and 60-day
averaging periods and the exposure measurement point is that averaging
period corresponding to a one in ten year return frequency for
estimating exposure to water column dwelling organisms.  This modeling
effort focuses on aerial and ground applications only, chemigation and
injection are not included specifically as there are not adequate
modeling scenarios.  It is expected that over the top aerial and ground
applications are adequate to represent injection and chemgation.  This
risk assessment will use this approach, although the results are likely
to be overestimates of exposure for such a stable compound as
chlorantraniliprole because the model uses up to 36 years of application
events.  

Dietary exposures for terrestrial vertebrates are estimated using the
T-REX model version 1.3.1.  Inputs for this model are presented in the
Environmental Fate and Transport Characterization section of this risk
assessment.  The exposure endpoint for terrestrial vertebrates from the
T-REX model’s output corresponds to an upper bound single day peak
concentration of pesticide in each of four generalized dietary items. 
These pesticide concentration estimates are then used for either direct
comparison with dietary effects endpoints or first converted to daily
oral dose estimates for feeding wildlife and then compared to daily dose
effects endpoints.  Mean concentrations associated with a peak pesticide
residue estimate may be used in the risk characterization to provide
additional context to risk assessment conclusions.  However, the results
of the initial screen for chlorantraniliprole indicate that this
additional step will not be required for this case.

For terrestrial vertebrate risks the T-REX model was used with an
assumption of a maximum 0.5 lb ai/acre single application rate.  This is
highest application rate from the proposed labels.  The assumption of a
single maximum application at the labeled crop limit also will allow for
consideration of the potential for systemic uptake of the pesticide,
which is suggested by the following label statement “DupontTM E2Y45SC
insecticide is a systemic product and will be transmitted upward into
the plant from root uptake.”  If no Agency risk concerns are
identified at this conservative level, no further refinement would be
warranted.



4.	Effects Measures

The screening-level risk assessment typically relies on a suite of
toxicity studies performed on a limited number of organisms from broad
taxonomic groups that are used as surrogates for a variety of taxa.  The
following presents the tested taxonomic group, its target taxa as a
surrogate, and the effects measures commonly used in screening risk
assessment

Tested			Surrogate			Effects Measures Employed 

Taxa	 		For				

Birds			all birds bird, reptiles, and	most sensitive species tested

			terrestrial amphibians		LD50, LC50, NOAEC for 			

							reproduction and growth

Mammals (rat)		all mammals			LD50, NOAEL for 			

							reproduction and growth

Freshwater fish	all fish aquatic amphibians	most sensitive species
tested

							LC50, NOAEC for 			

							reproduction and growth

Freshwater 		all freshwater invertebrates	most sensitive species tested

invertebrates						LC50, NOAEC for 			

							reproduction and growth

Estuarine/marine	all estuarine/marine		most sensitive species tested

Fish			fish				LC50, NOAEC for 			

							reproduction and growth

Estuarine/marine	all estuarine/marine		most sensitive species tested

invertebrates		invertebrates			LC50, NOAEC for 			

							reproduction and growth

Terrestrial 		all terrestrial invertebrates	LD50 

Invertebrate 						(not commonly a quantitative risk assessment)

Terrestrial plants	all terrestrial plants		most sensitive species tested


(monocot/dicot)					of monocot and dicot EC25, 		

							EC5/NOAEC

Aquatic Plants		all aquatic plants		most sensitive species tested 

(algae/vascular)					of algae and vascular EC50/EC25, 		

							EC5/NOAEC



IV. 	ANALYSIS

A. 	Environmental Fate and Transport Characterization

Chlorantraniliprole is persistent and mobile in terrestrial and aquatic
environments.   Extended chlorantraniliprole use is expected to cause
accumulation of residues in soil from year to year.  Major routes of
dissipation are expected to be alkaline-catalyzed hydrolysis,
photodegradation in water, leaching, and runoff.

Chlorantraniliprole is stable to hydrolytic degradation in pH 5 and 7
buffer solutions.  It does, however, undergo rapid hydrolysis in pH 9
buffer solution (MRID 46889017).  The major hydrolysis degradation
product is
(2-[3-Bromo-1-(3-chloro-2-pyridinyl)-1H-pyrazol-5-yl]-6-chloro-3,8
dimethyl-4(3H)-quinazolinone (IN-EQW78).  Photodegradation of
chlorantraniliprole is a predominant degradation pathway. 
Chlorantraniliprole has a half-life of 0.37 days in pH 7 buffer solution
and 0.31 days in natural water irradiated with a Xenon arc lamp (MRID
46889018).  In a water/sediment system, chlorantraniliprole had
photodegradation half-lives of 22 days in loamy sand sediment and 9.9
days in sandy loam sediment system (MRID 46889122).  The major
photodegradation products are IN-EQW78, IN-LBA22, IN-LBA24, and
IN-LBA23.  A minor photodegradation product was identified as IN-ECD73. 

Chlorantraniliprole is stable (t1/2 = 228 to 924 days) in aerobic soils
incubated at 250C (MRID 46889015, 46889014, 46889124).  It degrades
faster at higher soil temperatures of 34-350C and 490C (MRID 46889124,
46889015).  Major degradation products were identified as IN-F6L99,
IN-EVK64, IN-EQW78, IN-ECD73, IN-GAZ70.  Minor degradation products were
identified IF-F9N04 and IN-EVK64.  Chlorantraniliprole is also
persistent (t1/2= 231 and 125 days) under stratified redox test
conditions in a sand and loam sediment/water systems (MRID 46889016).  
The major degradation product was identified as IN-EQW78.  Minor
degradations products were identified as IN-F6L99, IN-F9N04, IN-GAZ70,
and IN-ECD73.  

Chlorantraniliprole is expected to be mobile in soil and aquatic
environments.  It has soil: water Freundlich batch equilibrium
adsorption coefficients of 1.22 (Koc=153, 1/n=1.0028) in a loamy sand
from Spain, 9.16 (Koc=509, 1/n=1.0434) in a silty clay loam from IA, 
1.36 (Koc=272, 1/n=0.8485) in a sandy loam from  MS, 1.59 (Koc= 526,
1/n=0.9370) in a loamy sand from GA, 2.34 (Koc=180, 1/n=0.9256) in a
loam from Italy (MRID 46889123).  Because there is a positive, linear
regression between Kd and soil organic carbon, it is appropriate to use
Koc for environmental fate modeling.



Laboratory Environmental Fate Data for Chlorantraniliprole 

Data	Units	 Value	Source 

Molecular Weight	g/mole	483.15

	Solubility	mg/L	1.023	MRID 46889026

Vapor Pressure	Torr	1.57E-13	DuPont 16517



Henrys Constant	atm m3/mol	3.1E-15	Estimated

Hydrolysis @ pH 7 	Days	Stable	MRID 46889017

Photodegradation in Water	Days	0.31 	MRID 46889018

Aerobic Soil Metabolism

	Days	577.61

537.3

374.6   

410.1

246.6

228.0

888.6

924.1

396.0	MRID 46889124

MRID 46889015

MRID 46889124

(Total Soil Extractable Residue @ 25oC) for benzo and pyrazole-labeled
chlorantraniliprole

Aerobic Aquatic Metabolism	Days	231

125	MRID 46889016

Anaerobic Aquatic

Metabolism	Days	208	DuPont 14568

Soil:Water  Coefficients (Average Koc)	L/g	153-loam sand

509-silty clay loam

272-sandy loam

526-loamy sand

180-loam

	MRID 46889123

1- EFED recalculated first-order half-lives for both benzo- and
pyrazole-labeled chlorantraniliprole. Half-lives values presented in the
OECD Chlorantranilipole Volume 3(1): Annex B, Environmental Fate and
Behavior. (mean = 491 (886, 539, 380, 233, 323, 629, 423, 518 days);
SD=203; t90, n-1 =1.417; N=8)

The following table presents the degradates associated with each fate
study.  Structures of the degradates, when available are appended to
this risk assessment.

Study	Degradation Product	Maximum Formation Percentage

(% of applied parent) 	Chemical Name

Hydrolysis

MRID 46889212	IN-EQW78	86.7 @ pH 9 
(2-[3-Bromo-1-(3-chloro-2-pyridinyl)-1H-pyrazol-5-yl]-6-chloro-3,8
dimethyl-4(3H)-quinazolinone

Photodegradation in Water

MRID 46889018	IN-EQW78	ND @ pH 7 buffer  solution

ND @ natural water,  sterile

	(2-[3-Bromo-1-(3-chloro-2-pyridinyl)-1H-pyrazol-5-yl]-6-chloro-3,8
dimethyl-4(3H)-quinazolinone

	IN-LBA22	52.1 @ pH 7 buffer  solution

3.4   @ natural water,  sterile





IN-LBA24	90.2 @ pH 7 buffer  solution

89.3   @ natural water,  sterile





IN-LBA23	40.8 @ pH 7 buffer  solution

51.4 @ natural water,  sterile



	Soil Metabolism

MRID 46889014

MRID 46889124

MRID 46889015	IN-F6L99	 2.1 @ 250C incubation

 5.2 @ 350C incubation

 4.2 @ 490C incubation

	N-Methyl-[3-bromo-1H-pyrazol-5-yl]carboxylic acid

	IN-EVK64	ND @ 250C incubation

 1.7 @ 350C incubation

 5.3 @ 490C incubation



IN-EQW78	9.5  @ 250C incubation

33.3 @ 350C incubation

71.6  @ 490C incubation
(2-[3-Bromo-1-(3-chloro-2-pyridinyl)-1H-pyrazol-5-yl]-6-chloro-3,8
dimethyl-4(3H)-quinazolinone

	IN-ECD73	4.9 @ 250C incubation

8.2 @ 350C incubation

9.1  @ 490C incubation
2-[3-bromo-1-(3-chloro-2-pyridinyl)-1H-pyrazole-5-yl]-6-chloro-3,8-dimet
hyl-4(3H)-quinazolinone

	INGAZ70	4.3 @ 250C incubation

7.4  @ 350C incubation

1.0 @ 490C incubation
2-[3-bromo-1-(3-chloro-2-pyridinyl)-1H-pyrazol-5-yl]-6-chloro-8-methyl-4
(1H)-quinazolinone

Water/Sediment

Metabolism

MRID 46889016

MRID 46889122	IN-EQW78	30.2 @ no photodegradation

40.9 @ photodegradation
(2-[3-Bromo-1-(3-chloro-2-pyridinyl)-1H-pyrazol-5-yl]-6-chloro-3,8
dimethyl-4(3H)-quinazolinone

	IN-F6L99	4.2 @ no photodegradation

ND @  photodegradation	5-bromo-N-methyl-1H-pyrazole-3-carboxamide

	IN-F9N04	2.7 @ no photodegradation

ND @ photodegradation
N-[2-(Aminocarbonyl)-4-chloro-6-methylphenyl]-3-bromo-1-(3-chloro-2-pyri
dinyl)1H-pyrazole-5-carboxamide

	IN-GAZ70	3.0 @ no photodegradation

ND @ photodegradation
2-[3-bromo-1-(3-chloro-2-pyridinyl)-1H-pyrazol-5-yl]-6-chloro-8-methyl-4
(1H)-quinazolinone

	IN-ECD73	4.7 @ no photodegradation

0.8 @ photodegradation
2-[3-bromo-1-(3-chloro-2-pyridinyl)-1H-pyrazole-5-yl]-6-chloro-3,8-dimet
hyl-4(3H)-quinazolinone

	INLBA22	11.1 @ no photodegradation

ND @ photodegradation



INLBA24	4.6 @ no photodegradation

1.5 @ photodegradation



INLNA23	2.3 @ no photodegradation

0.5 @ photodegradation

	

 Radiolabelled chlorantraniliprole (applied at 0.286 lbs ai/A ) had
half-lives of 181 to 222 days for dissipation studies in CA and Texas
bareground field dissipation studies. In the Texas study, degradation
products include IN-EQW78 (42% of applied @ Day 450), IN-GAZ70 (7% of
applied radioactivity), IN-ECD73 (9.5%@ Day 540), IN-F6L99 (5% @ Day
120). Most of radioactivity was detected in the surface 0 to 6 inch soil
layer.  In the California study, degradation products include IN-EQW78
(29% of applied @ Day 741), IN-ECD73 (6.8% of applied radioactivity@ Day
740), IN-GAZ70 (5.9%@ Day 300), IN-F6L99 (2.1% @ Day 531). Applied
radioactivity was detected with soil depth.  Maximum depth of
radioactivity detection was 30-36 inches soil layer (2.7% of applied
radioactivity @ Day 379).

Nonradiolabelled chlorantraniliprole (formulated as 35WG at 0.286 lbs
ai/A) had half-lives of  210 days in Minnesota study and 274 days in
Prince Edward Island study.  In the Minnesota study,  degradation
products included IN-EQW78 ( 3.8% of applied @ Day 0),  IN-ECD73 (4.1%@
Day 0) and IN-GAZ70 (4.1% day Day 0).  Routes of dissipation  for
chlorantraniliprole were identified as leaching (1% of applied @ 12 to
30 inches) and runoff (<6% of applied).  In the Prince Edward study,
IN-EQW78 (5.3% of applied @ Day 0),  IN-ECD73 (1.3%@ Day 0) and IN-GAZ70
(0.4% day Day 0). Chlorantranilipole was detected (<0.5% of applied) at
soil depths greater than 30 cm.       

Nonradiolabelled chlorantraniliprole (formulated as 20SC at 0.286 lbs
ai/A) on bareground plots had half-lives of  52 days in California
study, 206 days in the Texas study, 697 days in the New Jersey study,
and 1130 days in the Georgia study.  In the California study,
degradation products included IN-EQW78 ( 21% of applied @ Day 540) and 
IN-ECD73 (4.0%@ Day 540).  Chlorantranilipole residues were detected at
depth 18 inches (45 cm). In the Texas study, degradation products
included IN-EQW78 

(20% of applied @ Day 540) and  IN-ECD73 (2%@ Day 540). 
Chlorantranilipole residues were detected at depths >24 inches (<0.8% of
applied). In the New Jersey study, degradation products included
IN-EQW78 (9% of applied @ Day 475) and  IN-ECD73 (4%@ Day 541). 
Chlorantranilipole residues were detected at depths > 24 inches (1% of
applied).  In the Georgia study, degradation products included IN-EQW78
(12% of applied @ Day 540) and  IN-ECD73 (6%@ Day 540). 
Chlorantranilipole residues were detected at depths 12 to 18 inches
(~0.33 % of applied). 

1.  Aquatic Organism Exposure

The aquatic exposure assessment for
3-bromo-N-[4-chloro-2-methyl]-6-[(methylamino)
carbonyl]phenyl]-1-(3-chloro-2-pyridinyl)-[H-pyrazole-5-carboxamide
(chlorantraniliprole) was conducted using registrant submitted data. 
The aquatic exposure assessment is based on Tier II surface water
modeling (PRZM-EXAMS shell, PE5V01).  The modeling was conducted using
registrant-submitted environmental fate data.  

The surface water modeling was conducted using PE5V01.  The modeling was
conducted for only chlorantraniliprole. The modeling strategy was
designed to assess major crops and application conditions specified in
the Section 3 for chlorantraniliprole.    



a.	Surface Water

The PRZM/EXAMS input parameters for chlorantraniliprole are shown in the
table below.

PRZM/EXAMS Input Parameters for Chlorantraniliprole 

Data	Units	 Value	Source 	Comments

Molecular Weight	g/mole	483.15



Solubility	mg/L	1.023	MRID 46889026

	Vapor Pressure	Torr	1.57E-13	DuPont 16517



	Henrys Constant	atm m3/mol	3.1E-15	Estimated	Calculated via solubility
and vapor pressure

Hydrolysis @ pH 7 	Days	Stable	MRID 46889017

	Photodegradation in Water	days	0.31 	MRID 46889018

	Aerobic Soil Metabolism	Days	631.762,3	MRID 46889124

MRID 46889015

MRID 46889124

	Calculated 90th percentile of mean1

Mean= 509 days 

SD= 252 days

t= 1.40

n= 9

*Several reported half-lives in MRID 46889124

 were not used because of poor fit with first-order degradation  model 

Aerobic Aquatic Metabolism	Days	 341.13	MRID 46889016	Calculated 90th
percentile of mean1

Mean=  178 days 

SD=  74.95 days

t= 3.078

n=2

Anaerobic Aquatic

Metabolism	Days	208	DuPont 14568	Value represents single half-life
value4

Soil:Water  Coefficient (Koc)	L/g	328	MRID 46889123	Average Koc



1 tinput=Mean+(t90,n-1*SD)/√N-1

2- EFED recalculated first-order half-lives for both benzo- and
pyrazole-labeled chlorantraniliprole. The calculated half-lives are
based on aerobic soil metabolism data in non-sterile soil at 250C.
Half-lives used in the assessment include 577.6, 537.3, 374.6, 410.1,
246.6, 228, 888.6, 924.1, 396 days.  

3- The 90th percentile of the mean half-life for chlorantraniliprole was
600 days for half-lives values presented in the OECD Chlorantranilipole
Volume 3(1): Annex B, Environmental Fate and Behavior. (mean = 491 (
886, 539, 380, 233, 323, 629, 423, 518 days); SD=203; t90, n-1 =1.417;
N=8)

4- A single value half-life was used because of the insensitivity of
PRZM/EXAMS modeling to anaerobic aquatic metabolism half-lives.  

The Agency does not have exposure scenarios for aquatic modeling for all
use sites and locations in the country.  Therefore, Agency risk
assessments rely on a series of representative model scenarios to
represent a suite of use sites and locations.   Because the proposed
chlorantraniliprole labels propose a range of application rates with
various application approaches and crops, EFED conducted a comprehensive
modeling analysis of the recommended application conditions for
chlorantraniliprole.  This analysis provides a series of possible use
scenarios to assess the impact of application rate, application method,
and crop on DPX-E2Y45 concentrations in surface water. Application
conditions considered in the modeling are in the following table.

Application Conditions of Chlorantraniliprole for Various Crop Types
(Maximum Application Rate)

Scenario	Application Method	Single Application Rate

(lbs ai/A)	Number of Applications 	Application Interval

(days)	Annual Application Rate

(lbs ai/A)

DuPont™Corgen™SC

FL cabbage	Aerial/Ground Spray	0.065	3	3	0.20

FL cucumber

0.065	3	5	0.20

PA tomato

0.098	2	5	0.20

CA tomato

0.098	2	5	0.20

FL tomato

0.098	2	5	0.20

FL peppers

0.098	2	5	0.20

CA lettuce

0.065	3	3	0.20

DuPont™Altacor™ WG

CA cotton	Aerial/Ground Spray	0.099	2	5	0.20

NC cotton

0.099	2	5	0.20

MS cotton

0.099	2	5	0.20

NY grape

0.099	2	7	0.20

CA grape

0.099	2	7	0.20

NC apple

0.099	2	10	0.20

PA apple

0.099	2	10	0.20

OR apple

0.099	2	10	0.20

ID potato

0.066	3	5	0.20

ME potato

0.066	3	5	0.20

GA peach

0.099	2	7	0.20

MI cherry

0.099	2	7	0.20

DuPont™E2Y45 SC

Turf	Ground Spray	0.26	2	7	0.5

Turf	Ground Spray	0.026	19	7	0.5

Ornamental Flowers and Groundcover	Ground Spray	0.4992	

1	

NA	0.5

NA- not applicable



Tier II aquatic EECs for maximum chlorantraniliprole application rates
are shown in the next two tables.

PRZM/EXAMS  EECs for Application Conditions of
Chlo慲瑮慲楮楬牰汯⁥潦⁲慖楲畯⁳牃灯吠灹獥⠠慍楸
畭⁭敁楲污䄠灰楬慣楴湯删瑡⥥܇捓湥牡潩䄇灰楬慣楴
湯删瑡൥氨獢愠⽩⥁⌇䄠灰ݳ灁汰捩瑡潩⁮湉整癲污⠍
慤獹ܩ‱湩ㄠ‰敹牡䌠湯散瑮慲楴湯

(μg/L)







Peak	

21-day

average	

60-day

Average

FL cabbage	0.065	3	3	2.652	2.146	1.466

FL cucumber	0.065	3	5	5.693	4.939	3.748

PA tomato	0.098	2	5	1.513	1.306	1.136

CA tomato	0.098	2	5	1.080	0.922	0.702

FL tomato	0.098	2	5	3.660	3.001	2.312

FL peppers	0.098	2	5	6.749	5.683	4.425

CA lettuce	0.065	3	3	3.579	2.997	2.203

CA cotton	0.099	2	5	1.785	1.576	1.229

NC cotton	0.099	2	5	3.730	3.207	2.584

MS cotton	0.099	2	5	3.769	3.271	2.633

NY grape	0.099	2	7	1.389	1.197	1.041

CA grape	0.099	2	7	1.188	1.026	0.791

NC apple	0.099	2	10	1.359	1.153	0.917

PA apple	0.099	2	10	1.245	1.091	0.857

OR apple	0.099	2	10	0.786	0.674	0.558

ID potato	0.066	3	5	1.021	0.859	0.707

ME potato	0.066	3	5	1.558	1.392	1.319

GA peach	0.099	2	7	1.086	0.886	0.655

MI Cherry	0.099	2	7	1.035	0.907	0.758





PRZM/EXAMS  EECs for Application Conditions of Chlorantraniliprole for
Various Crop Types (Maximum Ground Application Rate)

Scenario	Application Rate

(lbs ai/A)	# Apps	Application Interval

(days)	1 in 10 year Concentration

(μg/L)







Peak	

21-day

average	

60-day

Average

FL cabbage	0.065	3	3	2.531	2.045	1.331

FL cucumber	0.065	3	5	5.624	4.860	3.695

PA tomato	0.098	2	5	1.280	1.097	0.914

CA tomato	0.098	2	5	0.731	0.619	0.473

FL tomato	0.098	2	5	3.436	2.817	2.198

FL peppers	0.098	2	5	6.501	5.475	4.234

CA lettuce	0.065	3	3	3.311	2.781	2.057

CA cotton	0.099	2	5	1.470	1.280	1.005

NC cotton	0.099	2	5	3.473	2.995	2.440

MS cotton	0.099	2	5	3.575	3.116	2.469

NY grape	0.099	2	7	1.189	1.025	0.889

CA grape	0.099	2	7	0.813	0.706	0.550

NC apple	0.099	2	10	0.999	0.852	0.689

PA apple	0.099	2	10	1.048	0.898	0.716

OR apple	0.099	2	10	0.410	0.365	0.304

ID potato	0.066	3	5	0.812	0.680	0.513

ME potato	0.066	3	5	1.350	1.195	1.092

GA peach	0.099	2	7	0.763	0.620	0.447

MI Cherry	0.099	2	7	0.867	0.739	0.596

FLTurf	0.26	2	7	0.837	0.707	0.531

FL Turf	0.026	19	7	0.753	0.644	0.488

PA Turf	0.26	2	7	1.102	0.985	0.769

PA Turf	0.026	19	7	1.624	1.357	1.023

CA Turf	0.26	2	7	0.654	0.554	0.416

CA Turf	0.026	19	7	0.766	0.669	0.544

CA Nursery	0.4992	1	NA	5.663	4.672	3.495

CA Residential	0.4992	1	NA	1.779	1.543	1.385

FL Nursery	0.4992	1	NA	9.785	8.136	6.203

MI Nursery	0.4992	1	NA	2.508	2.284	2.033

TN Nursery	0.4992	1	NA	10.981	9.126	6.778

NA- not applicable



b.	Monitoring Data

There are no surface or groundwater water monitoring data for
chlorantraniliprole because it is a new compound

2. 	Terrestrial Vertebrate Exposure

 

Terrestrial vertebrate exposures were estimated using the T-REX v 1.3.1
model.  Because of the very low toxicity of chlorantraniliprole to
mammals and birds, the risk assessment considered exposure estimates
only for a highly conservative assumed maximum single use scenario (0.5
lbs ai/acre).  A default dissipation half-life value of 35 days was
assumed, though it has no impact on peak residue estimates for a single
application scenario The following table shows the results of the
exposure estimate.

T-REX Predicted Dietary EECs for a One-Time Conservative 

Application of 0.5 lb ai/acre

Dietary-based EECs  (mg/kg-diet)

Short Grass 	120.0

Tall Grass 	55.0

Broadleaf plants/sm Insects	67.5

Fruits/pods/seeds/lg Insects	7.5



3.	Terrestrial Invertebrate Exposure

The Agency currently has no method for estimating exposure to non-target
terrestrial invertebrates.

4.	Terrestrial Plant Exposure

Exposures for terrestrial plants were estimated using the TERRPLANT
model.  The low water solubility of chlorantraniliprole leads to the use
of a runoff factor of 0.01 in the model.  Because of the low expected
toxicity of the pesticide to terrestrial plants, the exposure estimates
presented in the table below are based on a maximum single application
rate for both aerial and ground methods.  Four application methods were
considered ground spray application (0.5 lb/acre, 560 g/ha) to turf with
no soil incorporation, ground spray application (0.5 lb/acre, 560 g/ha) 
to ornamentals with soil incorporation to 6 inches depth (surrogate for
soil injection), foliar spray application (0.2 lb/acre, 114 g/ha) with
ground equipment and no incorporation, foliar spray application (0.2
lb/acre, 114 g/ha) with aerial equipment and no incorporation.  In all
cases the solubility limit of the pesticide was entered into the model
as 0.88 mg/L (pH 7).



Estimated Plant Exposures Under Maximum Single Application Scenarios 

Application Method/Rate	Total Loading  to Adjacent Areas (EEC = Sheet
Runoff +Drift)

g ai/ha	Total Loading to Semi-aquatic Areas (EEC = Channelized Runoff +
Drift) 

g ai/ha	DRIFT EEC   (for ground: application rate x 0.01) (for aerial:
application rate x 0.05)

g ai/ha

Ground Spray to Turf and ornamentals

Unincorporated/560 g/ha	11.2	61.6	5.6

Ground Spray to Turf and ornamentals

Incorporated to six inches/560 g/ha	6.5	14.9	5.6

Aerial spray unincorporated /224 g/ha 	13.44	33.6	11.2

Ground spray unincorporated /224 g/ha 	4.48	24.64	2.24



B.  	Effects Characterization

In agreement with international governmental partners associated with
registration efforts for this pesticide, ecological effects data
evaluation responsibilities are being met through the efforts of the
Pesticides Safety Directorate (PSD), UK.  The Agency is using the
results of the PSD review as they appear in the dossier for registration
in Europe.  Except where specifically reported, independent validation
of statistical results for effects studies was not performed during the
PSD reviews.



1.	Avian Toxicity

This risk assessment uses the summarized acute and chronic toxicity data
from Volume 3, Annex B.9: Ecotoxicology with the regulatory evaluation
and approval as completed by the PSD.  The full text of those summaries
and evaluations are available in the above volume.  Chlorantraniliprole,
degradates and formulated products can be characterized as being
practically non-toxic from the acute oral and dietary perspectives.

Available Bird Toxicity Data for Chlorantraniliprole, Formulations, and
Degradates 

Test Material Identification	Nature of Tested Material	Registrant Study
ID	Test Species 	Test Type	Endpoint Type	Effects Value Based on A.S.
Units of Active Substance

Chlorantraniliprole Technical	Technical	DuPont-14380	Anas platyrhynchos

(Mallard)	Subacute dietary	LC 50

NOAEC	>5620

5620	mg/kg diet

Chlorantraniliprole Technical	Technical	DuPont-14384	Anas platyrhynchos

(Mallard)	Reproduction	LOAEC (viable embryo reduction)

NOAEC	250

500	mg/kg diet

Chlorantraniliprole Technical	Technical	DuPont-14378	Colinus virginianus

(Northern bobwhite)	Acute oral dose	LD 50

NOAEL 	>2250

2250	mg/kg bw

Chlorantraniliprole Technical	Technical	DuPont-14379	Colinus virginianus

(Northern bobwhite)	Subacute dietary	LC 50

NOAEC)	>5620

5620	mg/kg diet

Chlorantraniliprole Technical	Technical	DuPont-14383	Colinus virginianus

(Northern bobwhite)	Reproduction	LOAEC (egsheell thinning)

NOAEC	250

120	mg/kg-diet

IN-EQW78	Technical metabolite	DuPont-18859	Colinus virginianus

(Northern bobwhite)	Acute oral dose	LD 50

NOAEL	>2250

2250	mg IN-EQW78/kg bw

Chlorantraniliprole 20SC	Formulated Product	DuPont-18945	Colinus
virginianus

(Northern bobwhite)	Acute oral dose	LD 50

NOAEL(transient clinical signs, no mortality)	>2000

432

	mg a.i./kg bw

Chlorantraniliprole 35WG	Formulated Product	DuPont-18946	Colinus
virginianus

(Northern bobwhite)	Acute oral dose	LD 50

NOAEL(transient clinical signs, no mortality)	>2250

486

	mg a.i./kg bw

Chlorantraniliprole 20SC	Formulated Product	DuPont-19420	Colinus
virginianus

(Northern bobwhite)	Subacute dietary	LC 50

NOAEC	>5620

5620	mg a.i./kg diet



The available data show no indications that formulated product,
metabolites, or degradates are more toxic than active ingredient.



2.	Mammalian Toxicity

Acute toxicity study effects for the technical active ingredient in
mammals are reported as follows:

	Acute Oral Toxicity LD50: >5000 mg/kg (Rat)	

Acute Dermal Toxicity LD50: >5000 mg/kg (Rat) 

	Acute Inhalation Toxicity LC50: >5.1 mg/L (Rat)

	 

Formulated products are as equally non-toxic following acute exposures
as is

technical chlorantraniliprole. A single dose of chlorantraniliprole 20SC
[200 g/L (w/v); 18.5% (w/w)] (chlorantraniliprole 20SC) was administered
by oral gavage to three fasted female rats at a dose of 5000 mg/kg. The
rats were dosed one at a time at a minimum of 48-hour intervals.  All
rats survived until the scheduled sacrifice. No clinical signs of
toxicity were observed, and no body weight loss occurred after dosing.
No gross lesions were present in the rats at necropsy.  A single dose of
chlorantraniliprole 35WG was administered by oral gavage to one fasted
female rat each at a dose of 175, 550, or 1750 mg/kg and to three fasted
female rats at a dose of 5000 mg/kg.   No deaths occurred. The rats
exhibited no clinical signs of toxicity during the study. No body weight
losses occurred after dosing. No gross lesions were present in the rats
at necropsy. For the purposes of this risk assessment, to facilitate a
comparison of estimated dietary residues with toxicity endpoints for
acute effects, the existing rate oral LD50 toxicity study was used to
estimate a dietary concentration of the pesticide that would correspond
to a daily oral dose equivalent to the LD50.  To accomplish this, a
conservative ingestion rate of 100 percent of the body weight was
applied.  The resulting estimated dietary acute toxicity endpoint is
>5000 mg/kg-diet [(>5000 mg/kg-bw)(1 kg-bw/1kg-diet) = >5000
mg/kg-diet].

In developmental toxicity studies in rats and rabbits,
chlorantraniliprole exhibited no effects on any parameter in pregnant
females or their offspring at levels up to and including the maximum
tested dose of 1,000 mg/kg bw/day.  The NOAEL for this study is 1,000
mg/kg/day.

No reproduction toxicity was observed in a two-generation reproduction
study with

chlorantraniliprole in rats.  No adverse effects were observed on
reproduction, fertility, sperm parameters, estrous cycle, litter size,
pup survival and developmental landmarks up to the maximum tested dose
of 20,000 ppm in the diet. There were no adverse histological findings
indicative of reproductive toxicity. There was a slight reduction in the
F1 pup (but not F2 pup) weight during lactation at the highest dose
level (mean maternal intake during lactation equal to 3118
mg/kg-bw/day); this was attributed, in part, to weight loss in one
dehydrated dam during lactation which had a litter with some of the
lowest pup weights. The slight change in pup weight was without
subsequent effects since overall body weight, weight gain and
development in F1 rats fed 20,000 ppm were similar to control animals. 
The NOAEC for this study is 20,000 ppm or 1000 mg/kg bw/day as a NOAEL
(estimated).

3.	Terrestrial Invertebrate Toxicity

This risk assessment uses the summarized acute and chronic toxicity data
from Volume 3, Annex B.9: Ecotoxicology with the regulatory evaluation
and approval as completed by the PSD.  The full text of those summaries
and evaluations are available in the above volume.

The available formulated product data, when adjusted for active
ingredient suggest that there is no practical difference between the
toxicity of active ingredient and formulated products to bees.

Available Terrestrial Invertebrate Toxicity Data for
Chlorantraniliprole, Formulations, and Degradates (data ordered by
species to facilitate comparisons of a.i. with degradates and products)

Test Material Identification	Nature of Tested Material 	Registrant Study
ID	Test Species 	Test Type	Endpoint Type	Effects Value Based on A.S.
Units of Active Substance

Chlorantraniliprole 20SC	Formulated Product	DuPont-18423	Aphidius
rhopalosiphi	Mortality and reproduction	LR 50 and ER 50	>750	g.
chlorantraniliprole/ha

Chlorantraniliprole 35WG	Formulated Product	DuPont-12405	Aphidius
rhopalosiphi	Mortality and reproduction	LR 50 and ER 50	>750	g.
chlorantraniliprole/ha

Chlorantraniliprole 35WG	Formulated Product	DuPont-12753	Apis mellifera

(Honeybee)	Semi-field	NOEC	156.16	g. chlorantraniliprole/ha

Chlorantraniliprole 35WG	Formulated Product	DuPont-14387	Apis mellifera

(Honeybee)	Acute oral	LD50	>0.119	mg. chlorantraniliprole/bee

Chlorantraniliprole 35WG	Formulated Product	DuPont*-14387	Apis mellifera

(Honeybee)	Acute contact	LD50	>0.100	mg. chlorantraniliprole/bee

Chlorantraniliprole 20SC	Formulated Product	DuPont-14388	Apis mellifera

(Honeybee)	semi-field	NOAEC	52.5	g. chlorantraniliprole/ha

Chlorantraniliprole 20SC	Formulated Product	DuPont-14706	Apis mellifera

(Honeybee)	semi-field	NOAEC	52.5	g. chlorantraniliprole/ha

Chlorantraniliprole 35WG	Formulated Product	DuPont-16269	Apis mellifera

(Honeybee)	Acute	Mortality <4%	112.5	g. chlorantraniliprole/ha

Chlorantraniliprole 20SC	Formulated Product	DuPont-16271	Apis mellifera

(Honeybee)	semi-field	NOAEC	>60	g chlorantraniliprole/ha

Chlorantraniliprole 20SC	Formulated Product	DuPont-16272	Apis mellifera

(Honeybee)	semi-field	NOAEC	>60	g chlorantraniliprole/ha

Chlorantraniliprole 20SC	Formulated Product	DuPont-17208	Apis mellifera

(Honeybee)	semi-field	NOAEC	60	g. chlorantraniliprole/ha

Chlorantraniliprole 20SC	Formulated Product	DuPont-17247	Apis mellifera

(Honeybee)	semi-field	LOAEC (mortality and decreased flight intensity)
>60	g. chlorantraniliprole/ha

Chlorantraniliprole 20SC	Formulated Product	DuPont-17248	Apis mellifera

(Honeybee)	semi-field	LOAEC (mortality and decreased flight intensity)
60	g. chlorantraniliprole/ha

Chlorantraniliprole Technical	Technical	DuPont-17582	Apis mellifera

(Honeybee)	Acute oral	LD 50

	>0.0274

>104.1

	μg/bee in water

μg/bee in acetone

chlorantraniliprole/bee

Chlorantraniliprole 20SC	Formulated Product	DuPont-18085	Apis mellifera

(Honeybee)	semi-field	NOAEC	60	g. chlorantraniliprole/ha

Chlorantraniliprole 20SC	Formulated Product	DuPont-18086	Apis mellifera

(Honeybee)	semi-field	LOAEC (mortality and decreased flight intensity)
60	g. chlorantraniliprole/ha

Chlorantraniliprole 20SC	Formulated Product	DuPont-18087	Apis mellifera

(Honeybee)	semi-field	NOAEC	60	g. chlorantraniliprole/ha

Chlorantraniliprole 20SC	Formulated Product	DuPont-18426	Apis mellifera

(Honeybee)	Acute oral	LD 50	>114.1	μg. chlorantraniliprole/bee

Chlorantraniliprole 20SC	Formulated Product	DuPont-17301	Chrysoperla
carnea

(Green lacewing) larvae	Mortality Reproduction	EC50 LOEC	120

120	g chlorantraniliprole/ha

Chlorantraniliprole 20SC	Formulated Product	DuPont-19746	Coccinella
septempunctata 

(Lady bird beetle)	Mortality

Reproduction	LOAEC

LOAEC	60

60	g. chlorantraniliprole/ha

Chlorantraniliprole 20SC	Formulated Product	DuPont-17300	Coccinella
septempunctata 

(Lady bird beetle) larvae	Mortality Reproduction	EC50 LOEC	<120

120	g. chlorantraniliprole/ha

Chlorantraniliprole 	Technical	DuPont-14398	Eisenia fetida 

(Earthworm)	Acute	LC 50	>1000	mg chlorantraniliprole /kg soil dry
weight.

IN-EQW78	Technical metabolite	DuPont-15389	Eisenia fetida 

(Earthworm)	Acute	LC 50	>1000	mg IN-EQW78/kg soil dry weight.

Chlorantraniliprole 35WG	Formulated Product	DuPont-16694	Eisenia fetida 

(Earthworm	Reproduction Growth	NOAEC	350	mg chlorantraniliprole /kg soil
dry weight.

IN-EQW78	Technical metabolite	DuPont-17093	Eisenia fetida 

(Earthworm	Reproduction Growth	NOAEC	1000	mg IN-EQW78/kg soil dry
weight.

IN-F6L99	Technical metabolite	DuPont-17631	Eisenia fetida 

(Earthworm)	Acute	LC 50	632.5	mg IN-F6L99/kg soil dry weight.

IN-ECD73	Technical metabolite	DuPont-17632	Eisenia fetida 

(Earthworm)	Reproduction Growth	NOAEC	1000	mg IN-ECD73/kg artificial
soil dry weight

IN-GAZ70	Technical metabolite	DuPont-17633	Eisenia fetida 

(Earthworm)	Reproduction Growth	NOAEC	1000	mg IN-GAZ70/kg soil dry
weight

Chlorantraniliprole 35WG	Formulated Product	DuPont-18817	Eisenia fetida 

(Earthworm)	Acute	LC 50 	>350	mg chlorantraniliprole/kg drysoil

Chlorantraniliprole 20SC	Formulated Product	DuPont-18818	Eisenia fetida 

(Earthworm)	Acute	LC 50 	>200	mg chlorantraniliprole/kg drysoil

Chlorantraniliprole 20SC	Formulated Product	DuPont-16532	Episyrphus
balteatus

(Hoverfly)	Mortality 	LR100	120	g chlorantraniliprole/ha

Chlorantraniliprole 20SC	Formulated Product	DuPont-18082	Episyrphus
balteatus

(Hoverfly)	Mortality Reproduction	LR 50 ER 50	12.6

13.3	g chlorantraniliprole/ha

Chlorantraniliprole 20SC	Formulated Product	DuPont-19747	Episyrphus
balteatus

(Hoverfly)	Mortality 1st treatment

Mortality 2nd treatment

Reproduction	<control

>control

NOAEL	60

60

60	G  chlorantraniliprole/ha twice with 7-day interval

Chlorantraniliprole 35WG	Formulated Product	DuPont-18084	Episyrphus
balteatus

(Hoverfly)	Mortality

Reproduction	LR50

ER 50	4.64

>4.4	g. chlorantraniliprole/ha

Chlorantraniliprole 35WG	Formulated Product	DuPont-20303	Episyrphus
balteatus

(Hoverfly)	Mortality 1st treatment

Mortality 2nd treatment

Reproduction	<control

<control

NOAEL	60

60

60	g. chlorantraniliprole/ha twice with 7-day interval

IN-EQW78	Technical metabolite	DuPont-16531	Folsomia candida 

(Springtail)	Reproduction	EC 50 NOEC	>100 

100 	mg IN-EQW78/kg dry soil

IN-ECD73	Technical metabolite	DuPont-17083	Folsomia candida 

(Springtail)	Reproduction	EC 50 NOEC	>100 

100 	mg IN-ECD73/kg dry soil

Chlorantraniliprole 	Technical	DuPont-18730	Folsomia candida 

(Springtail)	Reproduction	EC 50 NOEC	0.48 

0.39 	mg chlorantraniliprole /kg dry soil

Chlorantraniliprole	Technical	DuPont-19748	Hypoaspis aculeifer (mite)
Reproduction	NOAEC	100	mg chlorantraniliprole /kg dry soil

Chlorantraniliprole 20SC	Formulated Product	DuPont-18081 RV1	Orius
laevigatus	Mortality and reproduction	LR 50 & ER 50	>120	g.
chlorantraniliprole/ha

Chlorantraniliprole 35WG	Formulated Product	DuPont-12406	Typhlodromus
pyri	Mortality and reproduction	LR 50 and ER 50	>750	g.
chlorantraniliprole/ha

Chlorantraniliprole 20SC	Formulated Product	DuPont-14704	Typhlodromus
pyri	Mortality and reproduction	LR 50 ER 50	>750	g.
chlorantraniliprole/ha

Chlorantraniliprole 20SC	Formulated Product	DuPont-17312	Typhlodromus
pyri	Population study	NOAEC	750	g. chlorantraniliprole/ha

Chlorantraniliprole 35WG	Formulated Product	DuPont-14705	Typhlodromus
pyri	Population reduction (transient)	LOAEC	52.5	g.
chlorantraniliprole/ha

Chlorantraniliprole 20SC	Formulated Product	DuPont-18424	Typhlodromus
pyri	Mortality and reproduction	LR 50 and ER 50	>750	g.
chlorantraniliprole/ha



4. 	Terrestrial Plant Toxicity

This risk assessment uses the summarized acute and chronic toxicity data
from Volume 3, Annex B.9: Ecotoxicology with the regulatory evaluation
and approval as completed by the PSD.  The full text of those summaries
and evaluations are available in the above volume.

The following table presents the available terrestrial plant toxicity
data.

Available Terrestrial Plant Toxicity Data for Chlorantraniliprole,
Formulations, and Degradates

Test Material Identification	Nature of Tested Material	Registrant Study
ID	Test Species 	Test Type	Endpoint Type	Effects Value Based on A.S. 
Units of Active Substance

Chlorantraniliprole 20SC	Formulated Product	DuPont-19074	Zea mays (corn)

Avena sativa (oat)

Allium cepa (common onion)

Lolium perenne (perennial ryegrass)

Cucumis sativa (cucumber)

Brassica napus (rape)

Pisum sativum (pea)

Glycine max (soybean)

Beta vulgaris (sugarbeet)

Lycopersicon esculentum (tomato)	Vegetative vigor	EC25 dicots

EC5 dicots

EC25 monocots

EC5 monocots

	>300

>300 cucumber, rape

 <300 all others

>300 

<300 Onion

>300 otherl species

	g. chlorantraniliprole /ha

Chlorantraniliprole 20SC	Formulated Product	DuPont-19075	Zea mays (corn)

Avena sativa (oat)

Allium cepa (common onion)

Lolium perenne (perennial ryegrass)

Cucumis sativa (cucumber)

Brassica napus (rape)

Pisum sativum (pea)

Glycine max (soybean)

Beta vulgaris (sugarbeet)

Lycopersicon esculentum (tomato)	Seedling emergence	EC25 monocots

EC5 monocots

EC25 dicots

EC5 dicots

	

>300 (except rygrass with 34% effect)

<300 

<300 all others

>300 

<300 (cucumber, rape, pea, sugar beet)

>300 otherl species

	g. chlorantraniliprole /ha



5.	Freshwater Invertebrate Toxicity

This risk assessment uses the summarized acute and chronic toxicity data
from Volume 3, Annex B.9: Ecotoxicology with the regulatory evaluation
and approval as completed by the PSD.  The full text of those summaries
and evaluations are available in the above volume.  Chlorantraniliprole
can be characterized as very highly toxic to freshwater invertebrates.

Available Freshwater Invertebrate Toxicity Data for Chlorantraniliprole,
Formulations, and Degradates (data ordered by species to facilitate
comparisons of a.i. with degradates and products)

Test Material Identification	Nature of Tested Material	Registrant Study
ID	Test Species 	Test Type	Endpoint Type	Effects Value Based on A.S.
Units of Active Substance

Chlorantraniliprole Technical	Technical	DuPont-18428	Brachionus
calyciflorus	Acute	EC 50	>1.00	mg chlorantraniliprole/L

Chlorantraniliprole Technical	Technical	DuPont-15109	Centroptilum
triangulifer

(Mayfly)	Acute	LC 50	0.0116	mg chlorantraniliprole/L

Chlorantraniliprole Technical	Technical	DuPont-17585	Chimarra atterima

(Caddisfly)	Acute	LC 50	0.0117	mg chlorantraniliprole/L

Chlorantraniliprole Technical	Technical	DuPont-15112	Chironomus riparius

(Midge)	Acute	LC 50	0.0859	mg chlorantraniliprole/L

Chlorantraniliprole Technical	Technical	DuPont-14396	Chironomus riparius

(Midge)	Chronic	NOAEC (pore water from 28-d sediment study	0.005	mg
chlorantraniliprole/kg spiked sediment dry weight

Chlorantraniliprole Technical	Technical	DuPont-18090	Copepods (of the
suborder Cyclopoida)	Acute	LC 50	>1.00	mg chlorantraniliprole
technical/L

Chlorantraniliprole Technical	Technical	DuPont-15868	28-day old Daphnia
magna

(Water flea)	Acute	EC 50	0.0166	mg chlorantraniliprole/L

Chlorantraniliprole Technical	Technical	DuPont-12411*	Daphnia magna

(Water flea)	Acute	EC 50	0.0116	mg chlorantraniliprole/L

Chlorantraniliprole Technical	Technical	DuPont-12754 RV1	Daphnia magna

(Water flea)	Chronic	NOAEC	0.00447	mg chlorantraniliprole/L

LBA24-002	Technical metabolite	DuPont-14889 RV1	Daphnia magna

(Water flea)	Acute	EC 50

NOAEC	>10

10	mg LBA24-002/L

LBA22-002	Technical metabolite	DuPont-14890 RV1	Daphnia magna

(Water flea)	Acute	EC 50

NOAEC	>0.24

0.24	mg LBA22-002/L

Chlorantraniliprole 35WG	Formulated Product	DuPont-15113	Daphnia magna

(Water flea)	Acute	 EC 50	0.011	mg chlorantraniliprole/L

IN-EQW78	Technical metabolite	DuPont-15388	Daphnia magna

(Water flea)	Acute	EC 50

NOAEC	>0.138

0.138	mg IN-EQW78/L

Chlorantraniliprole Technical	Technical	DuPont-15874	Daphnia magna

(Water flea)	Chronic	NOAEC	0.00447	mg chlorantraniliprole/L

LBA23-000	 	DuPont-16754 RV1	Daphnia magna

(Water flea)	Acute	EC 50

NOAEC	>0.01	mg LBA23-000/L

Chlorantraniliprole Technical	Technical	DuPont-17653	Daphnia magna

(Water flea)	Acute	EC 50	0.0098	mg chlorantraniliprole/L

IN-GAZ70	Technical metabolite	DuPont-18387	Daphnia magna

(Water flea)	Acute	EC 50

NOAEC	>0.00987

0.00987	mg IN-GAZ70/L

Chlorantraniliprole 20SC	Formulated Product	DuPont-18427 RV1	Daphnia
magna

(Water flea)	Acute	EC 50	0.0071	mg chlorantraniliprole/L

IN-ECD73	Technical metabolite	DuPont-18472	Daphnia magna

(Water flea)	Acute	EC 50

NOAEC	>0.013

0.0138	mg IN-ECD73/L

IN-F6L99	Technical metabolite	DuPont-18473	Daphnia magna

(Water flea)	Acute	EC 50	46.8	mg IN-F6L99/L

IN-F9N04	Technical metabolite	DuPont-18474	Daphnia magna

(Water flea)	Acute	EC 50	0.03	mg IN-F9N04/L

Chlorantraniliprole Technical	Technical	DuPont-15877	Gammarus
pseudolimnaeus	Acute	LC 50	0.0351	mg chlorantraniliprole/L

Chlorantraniliprole Technical	Technical	DuPont-15114	Hyalella azteca
Acute	LC 50	>0.389	mg chlorantraniliprole/L

Chlorantraniliprole Technical	Technical	DuPont-15873	Lumbriculus
variegatus

(California blackworm)	Acute	LC 50	>1.49	mg chlorantraniliprole/L

Chlorantraniliprole Technical	Technical	DuPont-15872	Oronectes virilis

(Crayfish)	Acute	LC 50	>1.42	mg chlorantraniliprole/L

Chlorantraniliprole Technical	Technical	DuPont-18804	Soyedina
carolinensis

(Carolina Forestfly)	Acute	LC 50	>0.978	mg chlorantraniliprole/L



The available data show no indications that formulated product,
metabolites, or degradates are more toxic than active ingredient.



Freshwater Fish Toxicity

This risk assessment uses the summarized acute and chronic toxicity data
from Volume 3, Annex B.9: Ecotoxicology with the regulatory evaluation
and approval as completed by the PSD.  The full text of those summaries
and evaluations are available in the above volume.  While non-definitive
LC50 values are only available for chlorantraniliprole, it can be
characterized as being slightly to practically non-toxic to freshwater
fish.

 Available Freshwater Fish Toxicity Data for Chlorantraniliprole,
Formulations, and Degradates (data ordered by species to facilitate
comparisons of a.i. with degradates and products)

Test Material Identification	Nature of Tested Material	Registrant Study
ID	Test Species 	Test Type	Endpoint Type	Effects Value Based on A.S.
Units of Active Substance

Chlorantraniliprole Technical	Technical	DuPont-14278	Ictalurus punctatus

(Channel catfish)	Acute	LC 50	>13.4	mg chlorantraniliprole/L

Chlorantraniliprole Technical	Technical	DuPont-12333	Lepomis macrochirus

(Bluegill sunfish)	Acute	LC 50	>15.1	mg chlorantraniliprole/L

Chlorantraniliprole Technical	Technical	DuPont-12332	Oncorhynchus mykiss

(Rainbow trout)	Acute	LC 50	>13.8	mg chlorantraniliprole/L

Chlorantraniliprole Technical	Technical	DuPont-14279	Oncorhynchus mykiss

(Rainbow trout)	Chronic	NOAEC	0.11	mg chlorantraniliprole/L

Chlorantraniliprole 35WG	Formulated Product	DuPont-15396	Lepomis
macrochirus

(Bluegill sunfish)	Acute	LC 50	>1.19	mg chlorantraniliprole/L

Chlorantraniliprole 20SC	Formulated Product	DuPont-18602	Lepomis
macrochirus

(Bluegill sunfish)	Acute	LC 50	>1.84	mg chlorantraniliprole/L

Chlorantraniliprole 35WG	Formulated Product	DuPont-15386	Oncorhynchus
mykiss

(Rainbow trout)	Acute	LC 50	>1.09	mg chlorantraniliprole/L

Chlorantraniliprole 20SC	Formulated Product	DuPont-18601	Oncorhynchus
mykiss

(Rainbow trout)	Acute	LC 50	>2.16	mg chlorantraniliprole/ha

* Study reviewed by PSD at the time of risk assessment.

The available data show no indications that formulated products are more
toxic than active ingredient.



7.	Estuarine/Marine Invertebrate Toxicity

The following table presents the available estuarine/marine invertebrate
toxicity data.  This risk assessment uses the summarized acute and
chronic toxicity data from Volume 3, Annex B.9: Ecotoxicology with the
regulatory evaluation and approval as completed by the PSD.  The full
text of those summaries and evaluations are available in the above
volume.  Chrlorantraniliprole is very highly toxic to certain estuarine
marine invertebrates, based on the data for the eastern oyster.

Available Estuarine/Marine Invertebrate Toxicity Data for
Chlorantraniliprole, Formulations, and Degradates

Test Material Identification	Nature of Tested Material	Registrant Study
ID	Test Species 	Test Type	Endpoint Type	Effects Value Based on A.S.
Units of Active Substance

Chlorantraniliprole Technical	Technical	DuPont-12335	Americamysis bahia

(Mysid shrimp)	Acute	LC 50	1.15	mg chlorantraniliprole/L

Chlorantraniliprole Technical	Technical	DuPont-14397	Americamysis bahia

(Mysid shrimp)	Chronic	NOAEC	0.695	mg chlorantraniliprole/L

Chlorantraniliprole Technical	Technical	DuPont-12412	Crassostrea
virginica

(Eastern oyster)	Acute	EC 50	0.0399	mg chlorantraniliprole/L



Because the most sensitive species acutely (oyster) is not represented
by chronic values, the acute to chronic ratio for the mysid (1.15/0.695
= 1.65) was applied to the oyster LC50 to estimate a chronic effects
endpoint for this species (0.0399 mg/L/1.65 = 0.024 mg/L).



8.	Estuarine Marine Fish Toxicity

The following table presents the available estuarine/marine fish
toxicity data This risk assessment uses the summarized acute and chronic
toxicity data from Volume 3, Annex B.9: Ecotoxicology with the
regulatory evaluation and approval as completed by the PSD.  The full
text of those summaries and evaluations are available in the above
volume. While non-definitive LC50 values are only available for
chlorantraniliprole, it can be characterized as being slightly to
practically non-toxic to estuarine/marine fish.

Available Estuarine/Marine Fish Toxicity Data for Chlorantraniliprole,
Formulations, and Degradates

Test Material Identification	Nature of Tested Material	Registrant Study
ID	Test Species 	Test Type	Endpoint Type	Effects Value Based on A.S.
Units of Active Substance

Chlorantraniliprole Technical	Technical	DuPont-12334	Cyprinodon
variegatus

(Sheepshead minnow)	Acute	LC 50	>12.0	mg/L

Chlorantraniliprole Technical	Technical	DuPont-14394	Cyprinodon
variegatus

(Sheepshead minnow)	Early Life Stage Toxicity	NOAEC	1.28	mg/L





9.	Aquatic Plant Toxicity

The following table presents the available aquatic plant toxicity data. 
This risk assessment uses the summarized acute and chronic toxicity data
from Volume 3, Annex B.9: Ecotoxicology with the regulatory evaluation
and approval as completed by the PSD.  The full text of those summaries
and evaluations are available in the above volume.

Available Aquatic Plant Toxicity Data for Chlorantraniliprole,
Formulations, and Degradates

Test Material Identification	Nature of Tested Material	Registrant Study
ID	Test Species 	Test Type	Endpoint Type	Effects Value Based on A.S.
Units of Active Substance

Chlorantraniliprole Technical	Technical	DuPont-14390	Anabaena flos-aquae

(Blue-green algae)	Growth / Reproduction	EC50 NOAEC	>2

2	mg. chlorantraniliprole/L

Chlorantraniliprole Technical	Technical	DuPont-12409 RV1	Lemna gibba 

(Duckweed)	Growth / Reproduction	EC50 NOAEC	>2

2	mg. chlorantraniliprole/L

Chlorantraniliprole Technical	Technical	DuPont-14392 RV1	Navicula
pelliculosa	Growth / Reproduction	EC50

NOEC	>15.1

15.1	mg. chlorantraniliprole/L

Chlorantraniliprole Technical	Technical	DuPont-12408 RV1	Selenastrum
capricornutum

(Green algae)	Growth / Reproduction	EC50

NOEC	>2

2	mg. chlorantraniliprole/L

Chlorantraniliprole Technical	Technical	DuPont-14391	Skeletonema
costatum	Growth / Reproduction	EC50

NOEC	>14.6

14.6	mg. chlorantraniliprole/L

Chlorantraniliprole 20SC	Formulated Product	DuPont-18088
Pseudokirchneriella subcapitata

(Green algae)	Growth / Reproduction	EC50

NOEC	>4

4	mg. chlorantraniliprole/L

Chlorantraniliprole 35WG	Formulated Product	DuPont-18089
Pseudokirchneriella subcapitata

(Green algae)	Growth / Reproduction	EC50

NOEC	>1.78

1.78	mg. chlorantraniliprole/L





10.	Summary of Effects Measurement Endpoint Values Used in the Risk
Assessment

The following table presents the effects measurement endpoints used in
the risk assessment for chlorantraniliprole.

Effects Measurement Endpoints Used in Quantitative Risk Assessment

Taxa	Effects Measurement Endpoint	Rationale

Birds (reptiles, terrestrial invertebrates)	Survival – bobwhite and
mallard LC50>5620 mg/kg-diet

Reproduction – mallard 120 mg/kg-diet	Most sensitive tested

Most sensitive tested

Mammals	Survival – estimated rat LC50>5000 mg/kg-diet

Reproduction – rat NOAEC 20,000 mg/kg-diet	Most sensitive tested LD50
adjusted to estimate dietary equivalent (100% bw consumed/day)

Most sensitive tested

Terrestrial plants	Vegetative Vigor                Dicot EC25  >300 g/ha

                                      Dicot EC5 <300 g/ha

                                      Monocot EC25 >300g/ha

                                      Monocot EC5 <300g/ha

Seedling Emergence             Dicot EC25 >300 g/ha

                                      Dicot EC5 <300 g/ha

                                      Monocot EC25 <300 /ha

                                      Monocot EC5 <300 g/ha	Most
sensitive tested

Most sensitive tested

Most sensitive tested

Most sensitive tested

Most sensitive tested

Most sensitive tested

Most sensitive tested

Most sensitive tested

Freshwater invertebrates	Survival – daphnid 48-h EC50 0.0116 mg/L

Reproduction –daphnid NOAEC 0.0044 mg/L	Most sensitive tested

Most sensitive tested

Freshwater fish	Survival – trout 96-h LC50 > 13.8 mg/L

Reproduction – trout NOAEC 0.11 mg/L	Most sensitive tested

Most sensitive tested

Estuarine/marine

invertebrates	Survival – oyster 48-h EC50 0.0399 mg/L

Chronic effect estimate – 0.024 mg/L	Most sensitive tested

Most sensitive tested for acute adjusted with available ACR

Estuarine/marine fish	Survival– sheepshead 96-h LC50 > 12 mg/L

Reproduction – sheepshead NOAEC 1.28 mg/L	Most sensitive tested

Most sensitive tested

Aquatic plants	Growth/reproduction – Unicellular NOEC 1.78 mg/L

Growth – Vascular NOEC 2 mg/L	Most sensitive tested

Most sensitive tested





V. 	RISK CHARACTERIZATION

A. 	Risk Estimation

1.	Terrestrial Vertebrate Risk Quotients

Because of the very low toxicity of chlorantraniliprole to mammals and
birds, the risk assessment presents risk quotients (RQs) only for a
highly conservative assumed maximum single use scenario (0.5 lbs
ai/acre).  The following two tables show the results of these RQ
calculations.  No Agency levels of concern (LOCs) were exceeded for
birds or mammals under this upper bound exposure assumption.  There
would be no concern for labeled uses which are all of lower application.

Mammal RQs

Dietary Item	Estimated EEC

 mg/kg-diet	Acute Effects Endpoint mg/kg-diet	Chronic

Effects Endpoint mg/kg-diet	Acute RQ*	Chronic

RQ*	Identified Concerns**

Short Grass 	120.0	>5000	20,000	<0.1	<1	None

Tall Grass 	55.0

	<0.1	<1	None

Broadleaf plants/sm Insects	67.5

	<0.1	<1	None

Fruits/pods/seeds/lg Insects	7.5

	<0.1	<1	None

* RQ = EEC/effects endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5),
restricted use (0.2), and listed species (0.1).  Chronic RQs compared
with chronic LOC of 1.

Bird RQs

Dietary Item	Estimated EEC

 mg/kg-diet	Acute Effects Endpoint mg/kg-diet	Chronic

Effects Endpoint mg/kg-diet	Acute RQ*	Chronic

RQ*	Identified Concerns**

Short Grass 	120.0	>5620	500	<0.1	<1	None

Tall Grass 	55.0

	<0.1	<1	None

Broadleaf plants/sm Insects	67.5

	<0.1	<1	None

Fruits/pods/seeds/lg Insects	7.5

	<0.1	<1	None

* RQ = EEC/effects endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5),
restricted use (0.2), and listed species (0.1).  Chronic RQs compared
with chronic LOC of 1.

2.	Terrestrial Invertebrate Risk Quotients

The Agency currently does not have a method for calculating risk
quotients for terrestrial invertebrates.

3.	Terrestrial Plant Risk Quotients

Only the highest application scenario was modeled for plant exposures. 
For seedling emergence-based risk quotients runoff plus drift loading to
adjacent areas is directly compared with available toxicity endpoints
(see table below).  Because these endpoints were not definitive
endpoints it, numerical conclusions regarding exceeding Agency levels of
concern cannot be made.  Instead, the risk discussion section of this
document will provide further context.

Seedling Emergence Plant RQs Under Maximum Single Application Rate

Application Method/Rate	Total Loading  to Adjacent Areas

g ai/ha	Total Loading to Semi-aquatic Areas

g ai/ha	Plant Type	Non-Listed

Effects Endpoint

(g/ha)	Listed Effects Endpoint

(g/ha)	Non-Listed RQ	Listed RQ

Ground Unincorp./100.8 g/ha	2.0160	11.0880	Monocot

Dicot	<300

>300	<300

<300	>0.0067

<0.0067	>0.037

>0.037

Ground Incorp/100.8 g/ha	2.0160	11.0880	Monocot

Dicot	<300

>300	<300

<300	>0.0067

<0.0067	>0.037

>0.037

Aerial /100.8 g/ha	6.0480	15.1200	Monocot

Dicot	<300

>300	<300

<300	>0.020

<0.020

	>0.050

>0.050





For vegetative vigor-based risk quotients runoff plus drift loading to
adjacent areas is directly compared with available toxicity endpoints
(see table below).  Because these endpoints were not definitive
endpoints it, numerical conclusions regarding exceeding Agency levels of
concern cannot be made.  Instead, the risk discussion section of this
document will provide further context.

Vegetative Vigor Plant RQs Under Maximum Single Application Rate

Application Method/Rate	DRIFT EEC   (for ground: application rate x
0.01) (for aerial: application rate x 0.05)

g ai/ha	Plant Type	Non-Listed

Effects Endpoint

(g/ha)	Listed Effects Endpoint

(g/ha)	Non-Listed RQ	Listed RQ

Ground Unincorp./100.8 g/ha	1.0080	Monocot

Dicot	>300

>300	<300

<300	<0.0034

<0.0034

	>0.0034

>0.0034



Ground Incorp/100.8 g/ha	1.0080	Monocot

Dicot	>300

>300	<300

<300	<0.0034

<0.0034

	>0.0034

>0.0034



Aerial /100.8 g/ha	5.0400	Monocot

Dicot	>300

>300	<300

<300	<0.017

<0.017

	>0.017

>0.017





4.	Freshwater Fish Risk Quotients

The following tables present the RQs for freshwater fish.  No RQs
exceeded Agency levels of concern.

PRZM/EXAMS RQs  for FW Fish from Aerial Spray Application  of DPX-E2Y45
for Various Crop Types 

Scenario	Application	

Peak	

60-day

Average	Acute1 RQ	Chronic2

RQ	Identified

Concerns

	Rate

(lbs/A)	#	Int





	FL cabbage	0.065	3	3	2.652	1.466	0.0001	0.0133	None

FL cucumber	0.065	3	5	5.693	3.748	0.0003	0.0341	None

PA tomato	0.098	2	5	1.513	1.136	0.0001	0.0103	None

CA tomato	0.098	2	5	1.080	0.702	0.0001	0.0064	None

FL tomato	0.098	2	5	3.660	2.312	0.0002	0.0210	None

FL peppers	0.098	2	5	6.749	4.425	0.0003	0.0402	None

CA lettuce	0.065	3	3	3.579	2.203	0.0002	0.0200	None

CA cotton	0.099	2	5	1.785	1.229	0.0001	0.0112	None

NC cotton	0.099	2	5	3.730	2.584	0.0002	0.0235	None

MS cotton	0.099	2	5	3.769	2.633	0.0002	0.0239	None

NY grape	0.099	2	7	1.389	1.041	0.0001	0.0095	None

CA grape	0.099	2	7	1.188	0.791	0.0001	0.0072	None

NC apple	0.099	2	10	1.359	0.917	0.0001	0.0083	None

PA apple	0.099	2	10	1.245	0.857	0.0001	0.0078	None

OR apple	0.099	2	10	0.786	0.558	0.0000	0.0051	None

ID potato	0.066	3	5	1.021	0.707	0.0001	0.0064	None

ME potato	0.066	3	5	1.558	1.319	0.0001	0.0120	None

GA peach	0.099	2	7	1.086	0.655	0.0000	0.0060	None

MI Cherry	0.099	2	7	1.035	0.758	0.0001	0.0069	None

1-Acute Toxicity Endpoint=13,800 µg/L

2-Chronic Toxicity Endpoint=110 µg/L 

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5),
restricted use (0.1), and listed species (0.05).  Chronic RQs compared
with chronic LOC of 1.

PRZM/EXAMS RQs  for FW Fish from Ground Spray Application  of DPX-E2Y45
for Various Crop Types

Scenario	Application	

Peak	

60-day

Average	Acute1 RQ	Chronic2

RQ	Identified

Concerns

	Rate

(lb/A)	#	Int





	FL cabbage	0.065	3	3	2.531	1.331	0.0001	0.0121	None

FL cucumber	0.065	3	5	5.624	3.695	0.0003	0.0336	None

PA tomato	0.098	2	5	1.280	0.914	0.0001	0.0083	None

CA tomato	0.098	2	5	0.731	0.473	0.0000	0.0043	None

FL tomato	0.098	2	5	3.436	2.198	0.0002	0.0200	None

FL peppers	0.098	2	5	6.501	4.234	0.0003	0.0385	None

CA lettuce	0.065	3	3	3.311	2.057	0.0001	0.0187	None

CA cotton	0.099	2	5	1.470	1.005	0.0001	0.0091	None

NC cotton	0.099	2	5	3.473	2.440	0.0002	0.0222	None

MS cotton	0.099	2	5	3.575	2.469	0.0002	0.0224	None

NY grape	0.099	2	7	1.189	0.889	0.0001	0.0081	None

CA grape	0.099	2	7	0.813	0.550	0.0000	0.0050	None

NC apple	0.099	2	10	0.999	0.689	0.0000	0.0063	None

PA apple	0.099	2	10	1.048	0.716	0.0001	0.0065	None

OR apple	0.099	2	10	0.410	0.304	0.0000	0.0028	None

ID potato	0.066	3	5	0.812	0.513	0.0000	0.0047	None

ME potato	0.066	3	5	1.350	1.092	0.0001	0.0099	None

GA peach	0.099	2	7	0.763	0.447	0.0000	0.0041	None

MI Cherry	0.099	2	7	0.867	0.596	0.0000	0.0054	None

FLTurf	0.26	2	7	0.837	0.531	0.0000	0.0048	None

FL Turf	0.026	19	7	0.753	0.488	0.0000	0.0044	None

PA Turf	0.26	2	7	1.102	0.769	0.0001	0.0070	None

PA Turf	0.026	19	7	1.625	1.023	0.0001	0.0093	None

CA Turf	0.26	2	7	0.654	0.416	0.0000	0.0038	None

CA Turf	0.026	19	7	0.766	0.544	0.0000	0.0049	None

CA Nursery	0.4992	1	NA	5.663	3.495	0.0003	0.0318	None

CA Residential	0.4992	1	NA	1.779	1.385	0.0001	0.0126	None

FL Nursery	0.4992	1	NA	9.785	6.203	0.0004	0.0564	None

MI Nursery	0.4992	1	NA	2.508	2.033	0.0001	0.0185	None

TN Nursery	0.4992	1	NA	10.981	6.778	0.0005	0.0616	None

1-Acute Toxicity Endpoint=13,800 µg/L

2-Chronic Toxicity Endpoint=110 µg/L 

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5),
restricted use (0.1), and listed species (0.05).  Chronic RQs compared
with chronic LOC of 1.



5.	Freshwater Invertebrate Risk Quotients

The following table presents the RQs for freshwater invertebrates.

PRZM/EXAMS RQs  for FW Invertebrates from Aerial Spray Application  of
DPX-E2Y45 for Various Crop Types 

Scenario	Application	

Peak	

21-day

Average	Acute1 RQ	Chronic2

RQ	Identified

Concerns

	Rate

(lb/A)	#	Int





	FL cabbage	0.065	3	3	2.652	2.146	0.1850	0.4801	RU,LS

FL cucumber	0.065	3	5	5.693	4.939	0.4258	1.1049	RU,LS, C

PA tomato	0.098	2	5	1.513	1.306	0.1126	0.2922	RU,LS

CA tomato	0.098	2	5	1.080	0.922	0.0795	0.2063	LS

FL tomato	0.098	2	5	3.660	3.001	0.2587	0.6714	RU,LS

FL peppers	0.098	2	5	6.749	5.683	0.4899	1.2714	RU,LS,C

CA lettuce	0.065	3	3	3.579	2.997	0.2584	0.6705	RU,LS

CA cotton	0.099	2	5	1.785	1.576	0.1359	0.3526	RU,LS

NC cotton	0.099	2	5	3.730	3.207	0.2765	0.7174	RU,LS

MS cotton	0.099	2	5	3.769	3.271	0.2820	0.7318	RU,LS

NY grape	0.099	2	7	1.389	1.197	0.1032	0.2678	RU,LS

CA grape	0.099	2	7	1.188	1.026	0.0884	0.2295	LS

NC apple	0.099	2	10	1.359	1.153	0.0994	0.2579	LS

PA apple	0.099	2	10	1.245	1.091	0.0941	0.2441	LS

OR apple	0.099	2	10	0.786	0.674	0.0581	0.1508	LS

ID potato	0.066	3	5	1.021	0.859	0.0741	0.1922	LS

ME potato	0.066	3	5	1.558	1.392	0.1200	0.3114	RU,LS

GA peach	0.099	2	7	1.086	0.886	0.0764	0.1982	LS

MI Cherry	0.099	2	7	1.035	0.907	0.0782	0.2029	LS

1-Acute Toxicity Endpoint= 11.6 µg/L

2-Chronic Toxicity Endpoint= 4.47 µg/L 

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5),
restricted use (0.1), and listed species (0.05).  Chronic RQs compared
with chronic LOC of 1.



PRZM/EXAMS RQs  for FW Invertebrates from Ground Spray Application  of
DPX-E2Y45 for Various Crop Types 

Scenario	Application	

Peak	

21-day

Ave	Acute1 RQ	Chronic2

RQ	Identified

Concerns

	Rate

(lb/A)	#	Int





	FL cabbage	0.065	3	3	2.531	2.045	0.1763	0.4575	RU,LS

FL cucumber	0.065	3	5	5.624	4.86	0.4190	1.0872	RU,LS,C

PA tomato	0.098	2	5	1.280	1.097	0.0946	0.2454	LS

CA tomato	0.098	2	5	0.731	0.619	0.0534	0.1385	LS

FL tomato	0.098	2	5	3.436	2.817	0.2428	0.6302	RU,LS

FL peppers	0.098	2	5	6.501	5.475	0.4720	1.2248	RU,LS,C

CA lettuce	0.065	3	3	3.311	2.781	0.2397	0.6221	RU,LS

CA cotton	0.099	2	5	1.470	1.28	0.1103	0.2864	RU,LS

NC cotton	0.099	2	5	3.473	2.995	0.2582	0.6700	RU,LS

MS cotton	0.099	2	5	3.575	3.116	0.2686	0.6971	RU,LS

NY grape	0.099	2	7	1.189	1.025	0.0884	0.2293	LS

CA grape	0.099	2	7	0.813	0.706	0.0609	0.1579	LS

NC apple	0.099	2	10	0.999	0.852	0.0734	0.1906	LS

PA apple	0.099	2	10	1.048	0.898	0.0774	0.2009	LS

OR apple	0.099	2	10	0.410	0.365	0.0315	0.0817	None

ID potato	0.066	3	5	0.812	0.68	0.0586	0.1521	LS

ME potato	0.066	3	5	1.350	1.195	0.1030	0.2673	RU,LS

GA peach	0.099	2	7	0.763	0.62	0.0534	0.1387	LS

MI Cherry	0.099	2	7	0.867	0.739	0.0637	0.1653	LS

FLTurf	0.26	2	7	0.837	0.707	0.0609	0.1582	LS

FL Turf	0.026	19	7	0.753	0.644	0.0649	0.1441	LS

PA Turf	0.26	2	7	1.102	0.985	0.0849	0.2204	LS

PA Turf	0.026	19	7	1.625	1.357	0.1400	0.3036	RU,LS

CA Turf	0.26	2	7	0.654	0.554	0.0478	0.1239	None

CA Turf	0.026	19	7	0.766	0.669	0.0660	0.1500	LS

CA Nursery	0.4992	1	NA	5.663	4.672	0.4028	1.0452	RU,LS,C

CA Residential	0.4992	1	NA	1.779	1.543	0.1330	0.3452	RU,LS

FL Nursery	0.4992	1	NA	9.785	8.136	0.7014	1.8201	RU,LS,C

MI Nursery	0.4992	1	NA	2.508	2.284	0.1969	0.5110	RU,LS

TN Nursery	0.4992	1	NA	10.981	9.126	0.7867	2.0416	RU,LS,C

1-Acute Toxicity Endpoint=11.6 µg/L

2-Chronic Toxicity Endpoint= 4.47 µg/L 

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5),
restricted use (0.1), and listed species (0.05).  Chronic RQs compared
with chronic LOC of 1.

6.	Estuarine/Marine Fish Risk Quotients

The following table presents the RQs for estuarine/marine fish.  No
Agency levels of concern were exceeded.

PRZM/EXAMS RQs  for Estuarine/Marine Fish from Aerial Spray Application 
of DPX-E2Y45 for Various Crop Types 

Scenario	Application	

Peak	

60-day

Average	Acute1 RQ	Chronic2

RQ	Identified

Concerns

	Rate

(lb/A)	#	Int





	FL cabbage	0.065	3	3	2.652	1.466	0.0001	0.0011	None

FL cucumber	0.065	3	5	5.693	3.748	0.0003	0.0029	None

PA tomato	0.098	2	5	1.513	1.136	0.0001	0.0009	None

CA tomato	0.098	2	5	1.080	0.702	0.0001	0.0005	None

FL tomato	0.098	2	5	3.660	2.312	0.0002	0.0018	None

FL peppers	0.098	2	5	6.749	4.425	0.0004	0.0035	None

CA lettuce	0.065	3	3	3.579	2.203	0.0002	0.0017	None

CA cotton	0.099	2	5	1.785	1.229	0.0001	0.0010	None

NC cotton	0.099	2	5	3.730	2.584	0.0002	0.0020	None

MS cotton	0.099	2	5	3.769	2.633	0.0002	0.0021	None

NY grape	0.099	2	7	1.389	1.041	0.0001	0.0008	None

CA grape	0.099	2	7	1.188	0.791	0.0001	0.0006	None

NC apple	0.099	2	10	1.359	0.917	0.0001	0.0007	None

PA apple	0.099	2	10	1.245	0.857	0.0001	0.0007	None

OR apple	0.099	2	10	0.786	0.558	0.0000	0.0004	None

ID potato	0.066	3	5	1.021	0.707	0.0001	0.0006	None

ME potato	0.066	3	5	1.558	1.319	0.0001	0.0010	None

GA peach	0.099	2	7	1.086	0.655	0.0001	0.0005	None

MI Cherry	0.099	2	7	1.035	0.758	0.0001	0.0006	None

1-Acute Toxicity Endpoint=12,000 µg/L

2-Chronic Toxicity Endpoint= 1280 µg/L 

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5),
restricted use (0.1), and listed species (0.05).  Chronic RQs compared
with chronic LOC of 1.



PRZM/EXAMS RQs  for Estuarine/Marine Fish from Ground Spray Application 
of DPX-E2Y45 for Various Crop Types

Scenario	Application	

Peak	

60-day

Average	Acute1 RQ	Chronic2

RQ	Identified

Concerns

	Rate

(lb/A)	#	Int





	FL cabbage	0.065	3	3	2.531	1.331	0.0001	0.0010	None

FL cucumber	0.065	3	5	5.624	3.695	0.0003	0.0029	None

PA tomato	0.098	2	5	1.280	0.914	0.0001	0.0007	None

CA tomato	0.098	2	5	0.731	0.473	0.0000	0.0004	None

FL tomato	0.098	2	5	3.436	2.198	0.0002	0.0017	None

FL peppers	0.098	2	5	6.501	4.234	0.0004	0.0033	None

CA lettuce	0.065	3	3	3.311	2.057	0.0002	0.0016	None

CA cotton	0.099	2	5	1.470	1.005	0.0001	0.0008	None

NC cotton	0.099	2	5	3.473	2.440	0.0002	0.0019	None

MS cotton	0.099	2	5	3.575	2.469	0.0002	0.0019	None

NY grape	0.099	2	7	1.189	0.889	0.0001	0.0007	None

CA grape	0.099	2	7	0.813	0.550	0.0000	0.0004	None

NC apple	0.099	2	10	0.999	0.689	0.0001	0.0005	None

PA apple	0.099	2	10	1.048	0.716	0.0001	0.0006	None

OR apple	0.099	2	10	0.410	0.304	0.0000	0.0002	None

ID potato	0.066	3	5	0.812	0.513	0.0000	0.0004	None

ME potato	0.066	3	5	1.350	1.092	0.0001	0.0009	None

GA peach	0.099	2	7	0.763	0.447	0.0000	0.0003	None

MI Cherry	0.099	2	7	0.867	0.596	0.0000	0.0005	None

FLTurf	0.26	2	7	0.837	0.531	0.0000	0.0004	None

FL Turf	0.026	19	7	0.753	0.488	0.0000	0.0003	None

PA Turf	0.26	2	7	1.102	0.769	0.0001	0.0006	None

PA Turf	0.026	19	7	1.625	1.023	0.0001	0.0008	None

CA Turf	0.26	2	7	0.654	0.416	0.0000	0.0003	None

CA Turf	0.026	19	7	0.766	0.544	0.0000	0.0004	None

CA Nursery	0.4992	1	NA	5.663	3.495	0.0003	0.0027	None

CA Residential	0.4992	1	NA	1.779	1.385	0.0001	0.0011	None

FL Nursery	0.4992	1	NA	9.785	6.203	0.0005	0.0048	None

MI Nursery	0.4992	1	NA	2.508	2.033	0.0002	0.0016	None

TN Nursery	0.4992	1	NA	10.981	6.778	0.0006	0.0053	None

FLTurf	0.26	2	7	2.531	1.331	0.0001	0.0010	None

1-Acute Toxicity Endpoint=12,000 µg/L

2-Chronic Toxicity Endpoint= 1,280 µg/L 

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5),
restricted use (0.1), and listed species (0.05).  Chronic RQs compared
with chronic LOC of 1.

7.	Estuarine/Marine Invertebrate Risk Quotients

The following table presents the RQs for estuarine/marine invertebrates.

PRZM/EXAMS RQs  for Estuarine/Marine Invertebrates from Aerial Spray
Application  of DPX-E2Y45 for Various Crop Types 

Scenario	Application	

Peak	

21-day

Average	Acute1 RQ	Chronic2

RQ	Identified

Concerns

	Rate

(lb/A)	#	Int





	FL cabbage	0.065	3	3	2.652	2.146	0.0538	0.0894	LS

FL cucumber	0.065	3	5	5.693	4.939	0.1238	0.2058	RU,LS

PA tomato	0.098	2	5	1.513	1.306	0.0327	0.0544	None

CA tomato	0.098	2	5	1.080	0.922	0.0231	0.0384	None

FL tomato	0.098	2	5	3.660	3.001	0.0752	0.1250	LS

FL peppers	0.098	2	5	6.749	5.683	0.1424	0.2368	RU,LS

CA lettuce	0.065	3	3	3.579	2.997	0.0751	0.1249	LS

CA cotton	0.099	2	5	1.785	1.576	0.0395	0.0657	None

NC cotton	0.099	2	5	3.730	3.207	0.0804	0.1336	LS

MS cotton	0.099	2	5	3.769	3.271	0.0820	0.1363	LS

NY grape	0.099	2	7	1.389	1.197	0.0300	0.0499	None

CA grape	0.099	2	7	1.188	1.026	0.0257	0.0428	None

NC apple	0.099	2	10	1.359	1.153	0.0289	0.0480	None

PA apple	0.099	2	10	1.245	1.091	0.0273	0.0455	None

OR apple	0.099	2	10	0.786	0.674	0.0169	0.0281	None

ID potato	0.066	3	5	1.021	0.859	0.0215	0.0358	None

ME potato	0.066	3	5	1.558	1.392	0.0349	0.0580	None

GA peach	0.099	2	7	1.086	0.886	0.0222	0.0369	None

MI Cherry	0.099	2	7	1.035	0.907	0.0227	0.0378	None

1-Acute Toxicity Endpoint= 39.9 µg/L

2-Chronic Toxicity Endpoint= 24 µg/L 

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5),
restricted use (0.1), and listed species (0.05).  Chronic RQs compared
with chronic LOC of 1.



PRZM/EXAMS RQs  for Estuarine/Marine Invertebrates from Ground Spray
Application  of DPX-E2Y45 for Various Crop Types 

Scenario	Application	

Peak	

21-day

Average	Acute1 RQ	Chronic2

RQ	Identified

Concerns

	Rate

(lb/A)	#	Int





	FL cabbage	0.065	3	3	2.531	2.045	0.0513	0.0852	LS

FL cucumber	0.065	3	5	5.624	4.86	0.1218	0.2025	RU,LS

PA tomato	0.098	2	5	1.280	1.097	0.0275	0.0457	None

CA tomato	0.098	2	5	0.731	0.619	0.0155	0.0258	None

FL tomato	0.098	2	5	3.436	2.817	0.0706	0.1174	None

FL peppers	0.098	2	5	6.501	5.475	0.1372	0.2281	RU,LS

CA lettuce	0.065	3	3	3.311	2.781	0.0697	0.1159	LS

CA cotton	0.099	2	5	1.470	1.28	0.0321	0.0533	None

NC cotton	0.099	2	5	3.473	2.995	0.0751	0.1248	LS

MS cotton	0.099	2	5	3.575	3.116	0.0781	0.1298	LS

NY grape	0.099	2	7	1.189	1.025	0.0257	0.0427	None

CA grape	0.099	2	7	0.813	0.706	0.0177	0.0294	None

NC apple	0.099	2	10	0.999	0.852	0.0214	0.0355	None

PA apple	0.099	2	10	1.048	0.898	0.0225	0.0374	None

OR apple	0.099	2	10	0.410	0.365	0.0091	0.0152	None

ID potato	0.066	3	5	0.812	0.68	0.0170	0.0283	None

ME potato	0.066	3	5	1.350	1.195	0.0299	0.0498	None

GA peach	0.099	2	7	0.763	0.62	0.0155	0.0258	None

MI Cherry	0.099	2	7	0.867	0.739	0.0185	0.0308	None

FLTurf	0.26	2	7	0.837	0.707	0.0177	0.0295	None

FL Turf	0.026	19	7	0.753	0.644	0.0189	0.0268	None

PA Turf	0.26	2	7	1.102	0.985	0.0247	0.0410	None

PA Turf	0.026	19	7	1.625	1.357	0.0407	0.0565	None

CA Turf	0.26	2	7	0.654	0.554	0.0139	0.0231	None

CA Turf	0.026	19	7	0.766	0.669	0.0192	0.0279	None

CA Nursery	0.4992	1	NA	5.663	4.672	0.1171	0.1947	RU,LS

CA Residential	0.4992	1	NA	1.779	1.543	0.0387	0.0643	None

FL Nursery	0.4992	1	NA	9.785	8.136	0.2039	0.3390	RU,LS

MI Nursery	0.4992	1	NA	2.508	2.284	0.0572	0.0952	LS

TN Nursery	0.4992	1	NA	10.981	9.126	0.2287	0.3803	RU,LS

1-Acute Toxicity Endpoint=39.9 µg/L

2-Chronic Toxicity Endpoint= 24 µg/L 

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5),
restricted use (0.1), and listed species (0.05).  Chronic RQs compared
with chronic LOC of 1.

8.	Aquatic Plants

The following two tables present the RQs for aquatic plants.  No Agency
levels of concern were exceeded.

PRZM/EXAMS RQs  for Vascular Plants from Aerial Spray Application  of
DPX-E2Y45 for Various Crop Types

Scenario	Application	

Peak	Non-Listed

RQ	Listed

RQ	Identified

Concerns

	Rate

(lbs/A)	#	Int





FL cabbage	0.065	3	3	2.652	0.0013	0.0013	None

FL cucumber	0.065	3	5	5.693	0.0028	0.0028	None

PA tomato	0.098	2	5	1.513	0.0008	0.0008	None

CA tomato	0.098	2	5	1.080	0.0005	0.0005	None

FL tomato	0.098	2	5	3.660	0.0018	0.0018	None

FL peppers	0.098	2	5	6.749	0.0034	0.0034	None

CA lettuce	0.065	3	3	3.579	0.0018	0.0018	None

CA cotton	0.099	2	5	1.785	0.0009	0.0009	None

NC cotton	0.099	2	5	3.730	0.0019	0.0019	None

MS cotton	0.099	2	5	3.769	0.0019	0.0019	None

NY grape	0.099	2	7	1.389	0.0007	0.0007	None

CA grape	0.099	2	7	1.188	0.0006	0.0006	None

NC apple	0.099	2	10	1.359	0.0007	0.0007	None

PA apple	0.099	2	10	1.245	0.0006	0.0006	None

OR apple	0.099	2	10	0.786	0.0004	0.0004	None

ID potato	0.066	3	5	1.021	0.0005	0.0005	None

ME potato	0.066	3	5	1.558	0.0008	0.0008	None

GA peach	0.099	2	7	1.086	0.0005	0.0005	None

MI Cherry	0.099	2	7	1.035	0.0005	0.0005	None

1-Non-Listed Toxicity Endpoint=> 2,000 µg/L

2-Listed Toxicity Endpoint= 2,000µg/L 

* RQ = EEC/toxicity endpoint

** RQs  compared with  LOCs for non listed and listed species (1.0)

 



PRZM/EXAMS RQs  for Vascular Plants from Ground Spray Application  of
DPX-E2Y45 for Various Crop Types

Scenario	Application	

Peak	Non-Listed

RQ	Listed

RQ	Identified

Concerns

	Rate

(lbs/A)	#	Int





FL cabbage	0.065	3	3	2.531	0.0013	0.0013	None

FL cucumber	0.065	3	5	5.624	0.0028	0.0028	None

PA tomato	0.098	2	5	1.280	0.0006	0.0006	None

CA tomato	0.098	2	5	0.731	0.0004	0.0004	None

FL tomato	0.098	2	5	3.436	0.0017	0.0017	None

FL peppers	0.098	2	5	6.501	0.0033	0.0033	None

CA lettuce	0.065	3	3	3.311	0.0017	0.0017	None

CA cotton	0.099	2	5	1.470	0.0007	0.0007	None

NC cotton	0.099	2	5	3.473	0.0017	0.0017	None

MS cotton	0.099	2	5	3.575	0.0018	0.0018	None

NY grape	0.099	2	7	1.189	0.0006	0.0006	None

CA grape	0.099	2	7	0.813	0.0004	0.0004	None

NC apple	0.099	2	10	0.999	0.0005	0.0005	None

PA apple	0.099	2	10	1.048	0.0005	0.0005	None

OR apple	0.099	2	10	0.410	0.0002	0.0002	None

ID potato	0.066	3	5	0.812	0.0004	0.0004	None

ME potato	0.066	3	5	1.350	0.0007	0.0007	None

GA peach	0.099	2	7	0.763	0.0004	0.0004	None

MI Cherry	0.099	2	7	0.867	0.0004	0.0004	None

FLTurf	0.26	2	7	0.837	0.0004	0.0004	None

FL Turf	0.026	19	7	0.753	0.0004	0.0004	None

PA Turf	0.26	2	7	1.102	0.0006	0.0006	None

PA Turf	0.026	19	7	1.625	0.0008	0.0008	None

CA Turf	0.26	2	7	0.654	0.0003	0.0003	None

CA Turf	0.026	19	7	0.766	0.0004	0.0004	None

CA Nursery	0.4992	1	NA	5.663	0.0028	0.0028	None

CA Residential	0.4992	1	NA	1.779	0.0009	0.0009	None

FL Nursery	0.4992	1	NA	9.785	0.0049	0.0049	None

MI Nursery	0.4992	1	NA	2.508	0.0013	0.0013	None

TN Nursery	0.4992	1	NA	10.981	0.0055	0.0055	None

1-Non-Listed Toxicity Endpoint=> 2,000 µg/L

2-Listed Toxicity Endpoint= 2,000 µg/L 

* RQ = EEC/toxicity endpoint

**  RQs  compared with  LOCs for non listed and listed species (1.0)



PRZM/EXAMS RQs  for Unicellular Plants from Aerial Spray Application  of
DPX-E2Y45 for Various Crop Types

Scenario	Application	

Peak	Non-Listed

RQ	Listed

RQ	Identified

Concerns

	Rate

(lb/A)	#	Int





FL cabbage	0.065	3	3	2.652	0.0015	0.0015	None

FL cucumber	0.065	3	5	5.693	0.0032	0.0032	None

PA tomato	0.098	2	5	1.513	0.0009	0.0009	None

CA tomato	0.098	2	5	1.080	0.0006	0.0006	None

FL tomato	0.098	2	5	3.660	0.0021	0.0021	None

FL peppers	0.098	2	5	6.749	0.0038	0.0038	None

CA lettuce	0.065	3	3	3.579	0.0020	0.0020	None

CA cotton	0.099	2	5	1.785	0.0010	0.0010	None

NC cotton	0.099	2	5	3.730	0.0021	0.0021	None

MS cotton	0.099	2	5	3.769	0.0021	0.0021	None

NY grape	0.099	2	7	1.389	0.0008	0.0008	None

CA grape	0.099	2	7	1.188	0.0007	0.0007	None

NC apple	0.099	2	10	1.359	0.0008	0.0008	None

PA apple	0.099	2	10	1.245	0.0007	0.0007	None

OR apple	0.099	2	10	0.786	0.0004	0.0004	None

ID potato	0.066	3	5	1.021	0.0006	0.0006	None

ME potato	0.066	3	5	1.558	0.0009	0.0009	None

GA peach	0.099	2	7	1.086	0.0006	0.0006	None

MI Cherry	0.099	2	7	1.035	0.0006	0.0006	None

1-Non-Listed Toxicity Endpoint=> 1,780 µg/L

2-Listed Toxicity Endpoint= 1780µg/L 

* RQ = EEC/toxicity endpoint

** RQs  compared with  LOCs for non listed and listed species (1.0)



 

PRZM/EXAMS RQs  for  Unicellular Plants from Ground Spray Application 
of DPX-E2Y45 for Various Crop Types

Scenario	Application	

Peak	Non-Listed

RQ	Listed

RQ	Identified

Concerns

	Rate

(lb/A)	#	Int





FL cabbage	0.065	3	3	2.531	0.0014	0.0014	None

FL cucumber	0.065	3	5	5.624	0.0032	0.0032	None

PA tomato	0.098	2	5	1.280	0.0007	0.0007	None

CA tomato	0.098	2	5	0.731	0.0004	0.0004	None

FL tomato	0.098	2	5	3.436	0.0019	0.0019	None

FL peppers	0.098	2	5	6.501	0.0037	0.0037	None

CA lettuce	0.065	3	3	3.311	0.0019	0.0019	None

CA cotton	0.099	2	5	1.470	0.0008	0.0008	None

NC cotton	0.099	2	5	3.473	0.0020	0.0020	None

MS cotton	0.099	2	5	3.575	0.0020	0.0020	None

NY grape	0.099	2	7	1.189	0.0007	0.0007	None

CA grape	0.099	2	7	0.813	0.0005	0.0005	None

NC apple	0.099	2	10	0.999	0.0006	0.0006	None

PA apple	0.099	2	10	1.048	0.0006	0.0006	None

OR apple	0.099	2	10	0.410	0.0002	0.0002	None

ID potato	0.066	3	5	0.812	0.0005	0.0005	None

ME potato	0.066	3	5	1.350	0.0008	0.0008	None

GA peach	0.099	2	7	0.763	0.0004	0.0004	None

MI Cherry	0.099	2	7	0.867	0.0005	0.0005	None

FLTurf	0.26	2	7	0.837	0.0005	0.0005	None

FL Turf	0.026	19	7	0.753	0.0004	0.0004	None

PA Turf	0.26	2	7	1.102	0.0006	0.0006	None

PA Turf	0.026	19	7	1.625	0.0009	0.0009	None

CA Turf	0.26	2	7	0.654	0.0004	0.0004	None

CA Turf	0.026	19	7	0.766	0.0004	0.0004	None

CA Nursery	0.4992	1	NA	5.663	0.0032	0.0032	None

CA Residential	0.4992	1	NA	1.779	0.0010	0.0010	None

FL Nursery	0.4992	1	NA	9.785	0.0055	0.0055	None

MI Nursery	0.4992	1	NA	2.508	0.0014	0.0014	None

TN Nursery	0.4992	1	NA	10.981	0.0062	0.0062	None

1-Non-Listed Toxicity Endpoint=> 1,780 µg/L

2-Listed Toxicity Endpoint= 1,780 µg/L 

* RQ = EEC/toxicity endpoint

**  RQs  compared with  LOCs for non listed and listed species (1.0



B.	Risk Discussion

1.	Quantified Risks

The primary concerns for quantifiable risks associated with this
pesticide are for acute and chronic effects to aquatic invertebrates. 
The following table presents the proposed Section 3 uses associated with
RQ estimates for the model scenarios included in the quantitative
freshwater invertebrate risk assessment. 

Tier II RQs  for FW Invertebrates from Aerial Spray Application  of
DPX-E2Y45 for Various Crop Types 

Scenario	Application	

Peak	

21-day

Average	Acute1 RQ	Chronic2

RQ	Identified

Concerns

	lb/A	#	Int





	FL cabbage	0.065	3	3	2.652	2.146	0.1850	0.4801	RU,LS

FL cucumber	0.065	3	5	5.693	4.939	0.4258	1.1049	RU,LS, C

PA tomato	0.098	2	5	1.513	1.306	0.1126	0.2922	RU,LS

CA tomato	0.098	2	5	1.080	0.922	0.0795	0.2063	LS

FL tomato	0.098	2	5	3.660	3.001	0.2587	0.6714	RU,LS

FL peppers	0.098	2	5	6.749	5.683	0.4899	1.2714	RU,LS, C

CA lettuce	0.065	3	3	3.579	2.997	0.2584	0.6705	RU,LS

CA cotton	0.099	2	5	1.785	1.576	0.1359	0.3526	RU,LS

NC cotton	0.099	2	5	3.730	3.207	0.2765	0.7174	RU,LS

MS cotton	0.099	2	5	3.769	3.271	0.2820	0.7318	RU,LS

NY grape	0.099	2	7	1.389	1.197	0.1032	0.2678	RU,LS

CA grape	0.099	2	7	1.188	1.026	0.0884	0.2295	LS

NC apple	0.099	2	10	1.359	1.153	0.0994	0.2579	LS

PA apple	0.099	2	10	1.245	1.091	0.0941	0.2441	LS

OR apple	0.099	2	10	0.786	0.674	0.0581	0.1508	LS

ID potato	0.066	3	5	1.021	0.859	0.0741	0.1922	LS

ME potato	0.066	3	5	1.558	1.392	0.1200	0.3114	RU,LS

GA peach	0.099	2	7	1.086	0.886	0.0764	0.1982	LS

MI Cherry	0.099	2	7	1.035	0.907	0.0782	0.2029	LS

1-Acute Toxicity Endpoint= 11.6 µg/L

2-Chronic Toxicity Endpoint= 4.47 µg/L 

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5),
restricted use (0.1), and listed species (0.05).  Chronic RQs compared
with chronic LOC of 1.



Tier II RQs  for FW Invertebrates from Ground Spray Application  of
DPX-E2Y45 for Various Crop Types 

Scenario	Application	

Peak	

21-day

Average	Acute1 RQ	Chronic2

RQ	Identified

Concerns

	lb/a	#	Int





	FL cabbage	0.065	3	3	2.531	2.045	0.1763	0.4575	RU,LS

FL cucumber	0.065	3	5	5.624	4.86	0.4190	1.0872	RU,LS, 

PA tomato	0.098	2	5	1.280	1.097	0.0946	0.2454	LS

CA tomato	0.098	2	5	0.731	0.619	0.0534	0.1385	LS

FL tomato	0.098	2	5	3.436	2.817	0.2428	0.6302	RU,LS

FL peppers	0.098	2	5	6.501	5.475	0.4720	1.2248	RU,LS, C

CA lettuce	0.065	3	3	3.311	2.781	0.2397	0.6221	RU,LS

CA cotton	0.099	2	5	1.470	1.28	0.1103	0.2864	RU,LS

NC cotton	0.099	2	5	3.473	2.995	0.2582	0.6700	RU,LS

MS cotton	0.099	2	5	3.575	3.116	0.2686	0.6971	RU,LS

NY grape	0.099	2	7	1.189	1.025	0.0884	0.2293	LS

CA grape	0.099	2	7	0.813	0.706	0.0609	0.1579	LS

NC apple	0.099	2	10	0.999	0.852	0.0734	0.1906	LS

PA apple	0.099	2	10	1.048	0.898	0.0774	0.2009	LS

OR apple	0.099	2	10	0.410	0.365	0.0315	0.0817	None

ID potato	0.066	3	5	0.812	0.68	0.0586	0.1521	LS

ME potato	0.066	3	5	1.350	1.195	0.1030	0.2673	RU,LS

GA peach	0.099	2	7	0.763	0.62	0.0534	0.1387	LS

MI Cherry	0.099	2	7	0.867	0.739	0.0637	0.1653	LS

FLTurf	0.26	2	7	0.837	0.707	0.0609	0.1582	LS

PA Turf	0.26	2	7	1.102	0.985	0.0849	0.2204	LS

CA Turf	0.26	2	7	0.654	0.554	0.0478	0.1239	None

CA Nursery	0.4992	1	NA	5.663	4.672	0.4028	1.0452	RU,LS, C

CA Residential	0.4992	1	NA	1.779	1.543	0.1330	0.3452	RU,LS

FL Nursery	0.4992	1	NA	9.785	8.136	0.7014	1.8201	RU,LS, C

MI Nursery	0.4992	1	NA	2.508	2.284	0.1969	0.5110	RU,LS

TN Nursery	0.4992	1	NA	10.981	9.126	0.7867	2.0416	RU,LS, C

1-Acute Toxicity Endpoint=11.6 µg/L

2-Chronic Toxicity Endpoint= 4.47 µg/L 

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5),
restricted use (0.1), and listed species (0.05).  Chronic RQs compared
with chronic LOC of 1.



Acute concerns are triggered by freshwater invertebrate RQ values for
every exposure scenario modeled except the CA turf (ground spray) and OR
apple (ground spray).  These concerns are limited primarily to acute
effects to listed species and RQ values that are sufficiently high to
raise non-listed species concerns but within the manageable range for
restricted use considerations.  However, even for these proposed Section
3 uses, the restricted use concern level is just barely exceeded and no
exposure estimate reaches the median lethal concentration for the most
sensitive species tested.  

Chronic freshwater invertebrate risk concerns were identified for
proposed uses on  FL peppers (ground or aerial spray), FL cucumbers
(ground or aerial spray), CA nursery (ground spray), FL nursery (ground
spray), and TN nursery (ground spray).  In all cases the RQs were less
than an order of magnitude above the Agency concern level.  

Concerns to estuarine/marine invertebrates that exceed Agency concern
levels are confined to the following Tier II modeling scenarios: FL
cabbage (aerial or ground spray), FL cucumber (aerial or ground spray),
FL peppers (aerial or ground spray), FL tomatoes (aerial spray),  CA
lettuce (ground and aerial spray), NC cotton (aerial or ground spray),
MS cotton (aerial or ground spray) CA nursery (ground spray), TN nursery
(ground spray), FL nursery (ground spray), and MI nursery (ground
spray).  These risks are generally limited to acute effects to listed
species. However, the restricted use LOCs  are exceeded for the Florida
vegetable scenarios (cucumber, peppers) and nursery use scenarios (CA
nursery, TN nursery, and FL nursery scenarios). 



Tier II RQs  for Estuarine/Marine Invertebrates from Aerial Spray
Application  of DPX-E2Y45 for Various Crop Types 

Scenario	Application	

Peak	

21-day

Average	Acute1 RQ	Chronic2

RQ	Identified

Concerns

	lb/a	#	Int





	FL cabbage	0.065	3	3	2.652	2.146	0.0538	0.0894	LS

FL cucumber	0.065	3	5	5.693	4.939	0.1238	0.2058	RU,LS

PA tomato	0.098	2	5	1.513	1.306	0.0327	0.0544	None

CA tomato	0.098	2	5	1.080	0.922	0.0231	0.0384	None

FL tomato	0.098	2	5	3.660	3.001	0.0752	0.1250	LS

FL peppers	0.098	2	5	6.749	5.683	0.1424	0.2368	RU,LS

CA lettuce	0.065	3	3	3.579	2.997	0.0751	0.1249	LS

CA cotton	0.099	2	5	1.785	1.576	0.0395	0.0657	None

NC cotton	0.099	2	5	3.730	3.207	0.0804	0.1336	LS

MS cotton	0.099	2	5	3.769	3.271	0.0820	0.1363	LS

NY grape	0.099	2	7	1.389	1.197	0.0300	0.0499	None

CA grape	0.099	2	7	1.188	1.026	0.0257	0.0428	None

NC apple	0.099	2	10	1.359	1.153	0.0289	0.0480	None

PA apple	0.099	2	10	1.245	1.091	0.0273	0.0455	None

OR apple	0.099	2	10	0.786	0.674	0.0169	0.0281	None

ID potato	0.066	3	5	1.021	0.859	0.0215	0.0358	None

ME potato	0.066	3	5	1.558	1.392	0.0349	0.0580	None

GA peach	0.099	2	7	1.086	0.886	0.0222	0.0369	None

MI Cherry	0.099	2	7	1.035	0.907	0.0227	0.0378	None

1-Acute Toxicity Endpoint= 39.9 µg/L

2-Chronic Toxicity Endpoint= 24 µg/L 

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5),
restricted use (0.1), and listed species (0.05).  Chronic RQs compared
with chronic LOC of 1.



Tier II RQs  for Estuarine/Marine Invertebrates from Ground Spray
Application  of DPX-E2Y45 for Various Crop Types 

Scenario	Application	

Peak	

21-day

Average	Acute1 RQ	Chronic2

RQ	Identified

Concerns

	lb/A	#	Int





	FL cabbage	0.065	3	3	2.531	2.045	0.0513	0.0852	LS

FL cucumber	0.065	3	5	5.624	4.86	0.1218	0.2025	RU,LS

PA tomato	0.098	2	5	1.280	1.097	0.0275	0.0457	None

CA tomato	0.098	2	5	0.731	0.619	0.0155	0.0258	None

FL tomato	0.098	2	5	3.436	2.817	0.0706	0.1174	None

FL peppers	0.098	2	5	6.501	5.475	0.1372	0.2281	RU,LS

CA lettuce	0.065	3	3	3.311	2.781	0.0697	0.1159	LS

CA cotton	0.099	2	5	1.470	1.28	0.0321	0.0533	None

NC cotton	0.099	2	5	3.473	2.995	0.0751	0.1248	LS

MS cotton	0.099	2	5	3.575	3.116	0.0781	0.1298	LS

NY grape	0.099	2	7	1.189	1.025	0.0257	0.0427	None

CA grape	0.099	2	7	0.813	0.706	0.0177	0.0294	None

NC apple	0.099	2	10	0.999	0.852	0.0214	0.0355	None

PA apple	0.099	2	10	1.048	0.898	0.0225	0.0374	None

OR apple	0.099	2	10	0.410	0.365	0.0091	0.0152	None

ID potato	0.066	3	5	0.812	0.68	0.0170	0.0283	None

ME potato	0.066	3	5	1.350	1.195	0.0299	0.0498	None

GA peach	0.099	2	7	0.763	0.62	0.0155	0.0258	None

MI Cherry	0.099	2	7	0.867	0.739	0.0185	0.0308	None

FLTurf	0.26	2	7	0.837	0.707	0.0177	0.0295	None

PA Turf	0.26	2	7	1.102	0.985	0.0247	0.0410	None

CA Turf	0.26	2	7	0.654	0.554	0.0139	0.0231	None

CA Nursery	0.4992	1	NA	5.663	4.672	0.1171	0.1947	RU,LS

CA Residential	0.4992	1	NA	1.779	1.543	0.0387	0.0643	None

FL Nursery	0.4992	1	NA	9.785	8.136	0.2039	0.3390	RU,LS

MI Nursery	0.4992	1	NA	2.508	2.284	0.0572	0.0952	LS

TN Nursery	0.4992	1	NA	10.981	9.126	0.2287	0.3803	RU,LS

1-Acute Toxicity Endpoint=39.9 µg/L

2-Chronic Toxicity Endpoint= 24 µg/L 

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5),
restricted use (0.1), and listed species (0.05).  Chronic RQs compared
with chronic LOC of 1.



2.	Qualitative Discussion of Terrestrial Plant Risks

The lack of definitive EC5 or NOEC values for terrestrial plants renders
the risk conclusions for plants uncertain.  

Inhibition of seedling emergence was reduced 5 to 34% for monocot plant
species tested and from 0 to 18% for dicot species tested.   Non-listed
species RQs are within a fiftieth of Agency concern levels and within a
twentieth of listed species concerns, suggesting that the dose/response
curve for seedling emergence would have to be unusually steep for
predicted exposures to exceed non-listed plant concern levels.  
Confidence in the lack of risk concerns for listed species is less than
for non-listed plants, primarily because most species tested at single
concentration in the seedling emergence study exhibited effects well in
excess for the maximum 5% acceptable level for listed species.  Even
though exposures were well below the tested concentration, the
confidence in predicting that they would be associated with below a 5%
or less effect response is uncertain.

Similar statements can be made for risk predictions based on vegetative
vigor effects data, except that confidence that no non-listed plant
effects are expected as no tested monocot or dicot even approached the
25% effects level that would trigger non-listed plant concerns. 
However, listed plant RQ values are beyond an order of magnitude of
concern levels, but the finding that available effects data show
response as high as 12% inhibition in vegetative growth it is uncertain
whether predicted exposures would fall below thresholds triggering
concern for listed species (i.e., effects at or below 5%). Consequently
listed species plant concerns cannot be dismissed with available data.

3.	Qualitative Discussion of Terrestrial Invertebrate Risks

The Agency currently does not have a quantitative method to assess risks
of pesticides to non-target terrestrial invertebrates.  At first
principles, it would appear reasonable that an insecticide would pose
some risk to non-target terrestrial invertebrates, including non-target
insects.  The highest application rate of chlorantraniliprole in a year
is on the order of 200 g/ha.  Comparing this application rate to the
available insect toxicity data expressed in g of pesticide per hectare
suggests that acute effects on some insects (e.g. hoverfly, ladybird
beetles, and lacewings) are possible.  Therefore, the screening level
risk assessment conclusion is that effects on non-target insects cannot
be precluded. 

VI. 	FEDERALLY LISTED THREATENED AND ENDANGERED SPECIES ASSESSMENT

A.  	Action Area  TC "Action Area" \f C \l "3"  

  SEQ CHAPTER \h \r 1 For listed species assessment purposes, the action
area is considered to be the area affected directly or indirectly by the
Federal action and not merely the immediate area involved in the action.
 At the initial screening-level, the risk assessment considers broadly
described taxonomic groups and conservatively assumes that listed
species within those broad groups are located on or adjacent to the
treated site and aquatic organisms are assumed to be located in a
surface water body adjacent to the treated site.  The assessment also
assumes that the listed species are located within an assumed area which
has the relatively highest potential exposure to the pesticide, and that
exposures are likely to decrease with distance from the treatment area. 


If the assumptions associated with the screening-level action area
result in RQs that are below the listed species LOCs, a "no effect"
determination conclusion is made with respect to listed species in that
taxonomic group, and no further refinement of the action area is
necessary.  Furthermore, RQs below the listed species LOCs for a given
taxonomic group indicate no concern for indirect effects upon listed
species that depend upon the taxonomic group covered by the RQ as a
resource.  However, in situations where the screening assumptions lead
to RQs in excess of the listed species LOCs for a given taxonomic group,
a potential for a "may affect" conclusion exists and may be associated
with direct effects on listed species belonging to that taxonomic group
or may extend to indirect effects upon listed species that depend upon
that taxonomic group as a resource.  In such cases, additional
information on the biology of listed species, the locations of these
species, and the locations of use sites could be considered to determine
the extent to which screening assumptions regarding an action area apply
to a particular listed organism.  These subsequent refinement steps
could consider how this information would impact the action area for a
particular listed organism and may potentially include areas of exposure
that are downwind and downstream of the pesticide use site.

B.	Taxonomic Groups Potentially at Risk  TC "Taxonomic Groups
Potentially at Risk" \f C \l "3"  

  SEQ CHAPTER \h \r 1 The Level I screening assessment process for
listed species employs the generic taxonomic group-based process to make
inferences on direct effect concerns for listed species.  The first
iteration of reporting the results of the Level I screening is a listing
of pesticide use sites and taxonomic groups for which RQ calculations
reveal values that meet or exceed the listed species LOCs.  An
evaluation of risk conclusions for each taxonomic group is presented
below.

Potential Effects to Federally Listed Taxa





Listed Taxa	Direct Effects	Scenario Identified as of Concern	Indirect
Effects	Scenario Identified as of Concern

Terrestrial and semi-aquatic plants - monocots	Yes4

Yes1	all

Terrestrial and semi-aquatic plants - dicots	Yes4

Yes1	all

Terrestrial invertebrates	Yes	all	No

	Birds	No

Yes1,2,3,5	All 

Terrestrial phase amphibians	No

Yes1,2,5	All 

Reptiles	No

Yes1,2,3,5	All 

Mammals	No

Yes1,2,3,5	All 

Aquatic vascular plants	No

No

	Freshwater fish	No

Yes2,5	All 

Aquatic phase amphibians	No

Yes2,5	All 

Freshwater crustaceans	Yes	All except  CA turf (ground spray) and OR
apple (ground spray)	Yes2,5	All

Mollusks	Yes(may be subject to further evaluation)	All except  CA turf
(ground spray) and OR apple (ground spray)	Yes2,5	All

Marine/estuarine fish	No

Yes3	FL cabbage, FL cucumber, FL pepper, NC cotton, MS cotton,  CA
lettuce, CA nursery, FL nursery, MI nursery, TN nursery



Marine/estuarine invertebrates	Yes	FL cabbage, FL cucumber, FL pepper,
NC cotton, MS cotton,  CA lettuce, CA nursery, FL nursery, MI nursery,
TN nursery

	No

	1 direct effects on terrestrial invertebrates

2 direct effects on aquatic invertebrates

3 direct effects on estuarine/marine invertebrates

4 insufficient data to preclude risk

5direct effects to terrestrial plants at the listed species level of
concern suggests concern of animals with obligate relationships to a
plant species

C.	Analysis of Dose Response (Effects Study Slope)	

There was insufficient information in the PSD data reviews to establish
a definitive slope for acute toxicity studies supplying endpoints for
the calculation of risk quotients.  An assumed typical probit slope of
4.5 and an assumed range of 2 to 9 for this slope estimate were used to
estimate of individual mortality at when exposures for a taxonomic group
are at the listed species LOC.  Data for freshwater invertebrates
provided both a geometric mean slope and a range of measured values. 
These were used to estimate the changes of individual morality for the
freshwater invertebrate taxonomic group.

Slopes for animal endpoints and associated chance of individual
mortality associated with RQ = Acute Listed Species LOC

Taxa/acute study	Slope	Chance of Individual Mortality at 

RQ= Listed Species LOC	Confidence Intervals

Assumed slopes use slope interval 2 to 9

Measured slopes use measured range



Bird oral dose	

No mortality observed	Not calculated, no mortality observed	Not
calculated, no mortality observed

Bird dietary	No mortality observed	Not calculated, no mortality observed
Not calculated, no mortality observed

Mammal oral dose	No mortality observed	Not calculated, no mortality
observed	Not calculated, no mortality observed

Freshwater fish	No mortality observed	Not calculated, no mortality
observed	Not calculated, no mortality observed

Freshwater invertebrate	Assume 4.5	1 in  4.75E+02	1 in  1.73E+01 to  1
in  1.27E+03

Estuarine/marine fish	No mortality observed	Not calculated, no mortality
observed	Not calculated, no mortality observed

Estuarine/marine invertebrate	Assume 4.5	1 in  4.18E+08	1 in  2.16E+02
to <<1 in 1.0 E+16



D.	Consideration of Alternative Assumptions of Drift

In keeping with Agency policy, this screening risk assessment’s
aquatic exposure modeling assumes that spray drift loading to adjacent
aquatic systems comprises 5% (aerial application scenarios) and 1%
(ground application scenarios) of the field application rate.  In order
to see how important drift was to the ecological risk assessment
estimates, the aquatic exposure model was run both with assumed drift
and without for maximum single aerial application.  As can be seen from
the following able, drift accounts for 6% to 78% of estimated aquatic
concentrations, depending on the site and the averaging time.  This
would suggest that alternative assumption drift could have impact on the
overall risk estimation values. 

Comparison of Surface Water Concentration Model Results With and Without
a 5% Drift Assumption



Scenario	Peak EEC 	21 day average EEC	60 day average EEC

	with drift	without drift	Fraction of total as drift	with drift	without
drift	Fraction of total as drift	with drift	without drift	Fraction of
total as drift

FL cabbage	2.652	2.376	0.10	2.146	1.920	0.11	1.466	1.236	0.16

FL cucumber	5.693	5.327	0.06	4.939	4.598	0.07	3.748	3.497	0.07

PA tomato	1.513	1.159	0.23	1.306	0.994	0.24	1.136	0.828	0.27

CA tomato	1.080	0.625	0.42	0.922	0.519	0.44	0.702	0.391	0.44

FL tomato	3.660	3.212	0.12	3.001	2.632	0.12	2.312	2.058	0.11

FL peppers	6.749	6.117	0.09	5.683	5.152	0.09	4.425	3.976	0.10

CA lettuce	3.579	3.038	0.15	2.997	2.590	0.14	2.203	1.92	0.13

CA cotton	1.785	1.330	0.25	1.576	1.147	0.27	1.229	0.901	0.27

NC cotton	3.730	3,240	0.13	3.207	2.795	0.13	2.584	2.288	0.11

MS cotton	3.769	3.352	0.11	3.271	2.924	0.11	2.633	2.308	0.12

NY grape	1.389	1.085	0.22	1.197	0.936	0.22	1.041	0.797	0.23

CA grape	1.188	0.287	0.76	1.026	0.234	0.77	0.791	0.174	0.78

NC apple	1.359	0.864	0.36	1.153	0.738	0.36	0.917	0.600	0.35

PA apple	1.245	0.935	0.25	1.091	0.802	0.26	0.857	0.647	0.25

OR apple	0.786	0.377	0.52	0.674	0.334	0.50	0.558	0.278	0.50

ID potato	1.021	0.722	0.29	0.859	0.603	0.30	0.707	0.452	0.36

ME potato	1.558	1.264	0.19	1.392	1.106	0.21	1.319	0.983	0.25

GA peach	1.086	0.647	0.40	0.886	0.526	0.41	0.655	0.379	0.42

MI Cherry	1.035	0.793	0.23	0.907	0.674	0.26	0.758	0.531	0.30



AgDrift modeling at the Tier 1 series of assumptions shows that water
bodies (the standard assessment pond) adjacent to sprayed fields may
receive between 6.99% (coarse spray) to 24.25% (very fine spray) of the
aerially applied field rate through spray drift.  These values would
raise loadings from the assumed 5% by factors ranging from 1.4 to 4.9. 
Assuming a range of  6% to 78 % of total loadings could be attributable
to drift, accounting for higher drift fractions could  increase EEC
estimates and resulting RQ values by  1 to 3X.  These values would be
insufficient to trigger any additional concerns for aquatic vertebrates.
 It could increase freshwater invertebrate risks to include a more
frequent triggering of the non-listed acute risk concern.  Higher drift
assumptions could increase the number of sites triggering listed species
acute concerns for estuarine/marine invertebrates.  However, without
more site-specific evaluations, it is not possible to ascertain which
additional use areas would be of concern for estuarine marine
invertebrate risks.

E.	Critical Habitat

In the evaluation of pesticide effects on designated critical habitat,
consideration is given to the physical and biological features (primary
constituent elements) of a critical habitat identified by the U.S Fish
and Wildlife and National Marine Fisheries Services as essential to the
conservation of a listed species and which may require special
management considerations or protection.  The evaluation of impacts for
a screening level pesticide risk assessment focuses on the biological
features that are primary constituent elements and is accomplished using
the screening-level taxonomic analysis (RQs) and listed species’
levels of concern (LOCs) that are used to evaluate direct and indirect
effects to listed organisms.

The screening-level risk assessment for chlorantraniliprole has
identified potential concerns for direct and indirect effects on listed
species for those organisms dependant upon  a variety of taxonomic
groups.  In light of the potential for indirect effects, the next step
for EPA and the Service(s) is to identify which listed species and
critical habitat are potentially implicated.

Analytically, the identification of such species and critical habitat
can occur in either of two ways.  First, the agencies could determine
whether the action area overlaps critical habitat or the occupied range
of any listed species.  If so, EPA would examine whether the pesticide's
potential impacts on non-endangered species would affect the listed
species indirectly or directly affect a primary constituent element of
the critical habitat.  Alternatively, the agencies could determine which
listed species depend on biological resources, or have constituent
elements that fall into the taxa that may be directly or indirectly
impacted by a pesticide.  Then EPA would determine whether or not use of
the pesticide overlaps the critical habitat or the occupied range of
those listed species.  At present, the information reviewed by EPA is
not sufficient to permit use of either analytical approach to make a
definitive identification of species that are potentially impacted
indirectly or critical habitats that are potentially impacted directly
by the use of pesticides.  EPA and the Service(s) are working together
to conduct the necessary analysis.

This screening-level risk assessment for critical habitat provides a
listing of potential biological features that, if they are primary
constituent elements of one or more critical habitats, would be of
potential concern.  Risk to a variety of taxa exceeded the LOCs;
therefore, they were identified as being of potential concern for
indirect effects.  These results may be used to develop a problem
formulation for further assessment of critical habitat impacts outlined
above, should additional work be necessary.



F.	Co-Location Analysis

Appended to this document is a listing of federally listed threatened
and endangered species from the direct and indirect potentially affected
taxonomic groups.  This list was generated using the Agency’s LOCATES
database.



APPENDIX A

Available Structures for Degradates 









APPENDIX B-PRZM-EXAMS OUTPUT

APPENDIX

PRZM/EXAM OUTPUT

Surface Water Modeling

CA Nursey

stored as CAnursey.out

Chemical: DPXE2Y45

PRZM environment: CAnurserySTD.txt	modified Wedday, 24 January 2007 at
09:18:18

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w23188.dvf	modified Wedday, 3 July 2002 at 09:04:22

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.3087	0.2961	0.2598	0.1896	0.155	0.07079

1962	0.3588	0.3454	0.2966	0.2215	0.1848	0.08507

1963	0.8084	0.7755	0.6574	0.4897	0.4217	0.1773

1964	0.2993	0.2872	0.2436	0.1929	0.161	0.0639

1965	1.278	1.229	1.054	0.8463	0.7108	0.2686

1966	1.919	1.838	1.546	1.306	1.131	0.3364

1967	0.8282	0.802	0.7058	0.5636	0.556	0.2682

1968	4.709	4.516	3.824	2.771	2.274	0.8007

1969	0.4603	0.4432	0.3816	0.2895	0.2845	0.1361

1970	0.7214	0.6923	0.5879	0.4391	0.3612	0.148

1971	0.8821	0.8482	0.7259	0.5475	0.4586	0.2294

1972	0.3687	0.3576	0.3057	0.219	0.1755	0.1099

1973	0.8953	0.8636	0.7887	0.6198	0.5252	0.2212

1974	0.9828	0.9462	0.816	0.6005	0.4991	0.2207

1975	4.22	4.069	3.6	2.676	2.221	0.8166

1976	1.266	1.215	1.032	0.8465	0.7557	0.3072

1977	2.485	2.39	2.046	1.521	1.251	0.5434

1978	2.242	2.167	1.998	1.531	1.267	0.4622

1979	1.146	1.101	0.9936	0.8308	0.6962	0.2562

1980	1.799	1.725	1.46	1.094	0.9067	0.3227

1981	7.807	7.505	6.723	5.058	4.202	1.474

1982	5.768	5.552	4.766	3.575	2.99	1.103

1983	5.796	5.614	4.828	3.586	2.953	1.055

1984	0.3583	0.3446	0.2953	0.2338	0.1988	0.09669

1985	1.667	1.599	1.445	1.017	0.6826	0.2238

1986	1.542	1.506	1.345	1.075	0.9133	0.4214

1987	0.5282	0.5075	0.4328	0.3233	0.2951	0.1451

1988	1.896	1.821	1.561	1.134	0.9401	0.3569

1989	0.8781	0.8427	0.7164	0.5272	0.4413	0.1864

1990	0.5054	0.4894	0.437	0.3371	0.3495	0.1661

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	7.807	7.505	6.723	5.058	4.202	1.474

0.0645161290322581	5.796	5.614	4.828	3.586	2.99	1.103

0.0967741935483871	5.768	5.552	4.766	3.575	2.953	1.055

0.129032258064516	4.709	4.516	3.824	2.771	2.274	0.8166

0.161290322580645	4.22	4.069	3.6	2.676	2.221	0.8007

0.193548387096774	2.485	2.39	2.046	1.531	1.267	0.5434

0.225806451612903	2.242	2.167	1.998	1.521	1.251	0.4622

0.258064516129032	1.919	1.838	1.561	1.306	1.131	0.4214

0.290322580645161	1.896	1.821	1.546	1.134	0.9401	0.3569

0.32258064516129	1.799	1.725	1.46	1.094	0.9133	0.3364

0.354838709677419	1.667	1.599	1.445	1.075	0.9067	0.3227

0.387096774193548	1.542	1.506	1.345	1.017	0.7557	0.3072

0.419354838709677	1.278	1.229	1.054	0.8465	0.7108	0.2686

0.451612903225806	1.266	1.215	1.032	0.8463	0.6962	0.2682

0.483870967741936	1.146	1.101	0.9936	0.8308	0.6826	0.2562

0.516129032258065	0.9828	0.9462	0.816	0.6198	0.556	0.2294

0.548387096774194	0.8953	0.8636	0.7887	0.6005	0.5252	0.2238

0.580645161290323	0.8821	0.8482	0.7259	0.5636	0.4991	0.2212

0.612903225806452	0.8781	0.8427	0.7164	0.5475	0.4586	0.2207

0.645161290322581	0.8282	0.802	0.7058	0.5272	0.4413	0.1864

0.67741935483871	0.8084	0.7755	0.6574	0.4897	0.4217	0.1773

0.709677419354839	0.7214	0.6923	0.5879	0.4391	0.3612	0.1661

0.741935483870968	0.5282	0.5075	0.437	0.3371	0.3495	0.148

0.774193548387097	0.5054	0.4894	0.4328	0.3233	0.2951	0.1451

0.806451612903226	0.4603	0.4432	0.3816	0.2895	0.2845	0.1361

0.838709677419355	0.3687	0.3576	0.3057	0.2338	0.1988	0.1099

0.870967741935484	0.3588	0.3454	0.2966	0.2215	0.1848	0.09669

0.903225806451613	0.3583	0.3446	0.2953	0.219	0.1755	0.08507

0.935483870967742	0.3087	0.2961	0.2598	0.1929	0.161	0.07079

0.967741935483871	0.2993	0.2872	0.2436	0.1896	0.155	0.0639

0.1	5.6621	5.4484	4.6718	3.4946	2.8851	1.03116

					Average of yearly averages:	0.369098333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CAnursey

Metfile:	w23188.dvf

PRZM scenario:	CAnurserySTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.5591	kg/ha

Application Efficiency:	APPEFF	0.99	fraction

Spray Drift	DRFT	0.01	fraction of application rate applied to pond

Application Date	Date	1-3	dd/mm or dd/mmm or dd-mm or dd-mmm

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

CA Residential

stored as CAresidential.out

Chemical: DPXE2Y45

PRZM environment: CAresidential.txt	modified Tueday, 20 February 2007 at
12:04:34

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w23234.dvf	modified Wedday, 3 July 2002 at 09:04:22

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.5404	0.5281	0.4654	0.4019	0.38	0.2314

1962	1.562	1.529	1.388	1.129	0.9753	0.4413

1963	1.781	1.717	1.546	1.272	1.165	0.5281

1964	1.628	1.589	1.374	1.024	0.8675	0.4046

1965	0.5824	0.5671	0.5065	0.415	0.3696	0.2223

1966	0.514	0.4982	0.4638	0.3742	0.3476	0.2211

1967	3.914	3.777	3.582	2.753	2.367	0.9559

1968	1.234	1.193	1.06	0.8829	0.7864	0.3947

1969	1.288	1.257	1.183	1.082	0.9418	0.4011

1970	1.405	1.374	1.264	1.007	0.8713	0.3842

1971	0.4374	0.4227	0.3947	0.3497	0.3327	0.2185

1972	0.3352	0.3234	0.2805	0.2556	0.2482	0.1846

1973	1.759	1.699	1.5	1.341	1.187	0.5039

1974	0.6929	0.6693	0.5862	0.4708	0.4481	0.2708

1975	0.7903	0.7655	0.6905	0.5696	0.5511	0.2978

1976	0.604	0.582	0.523	0.4394	0.4065	0.2403

1977	1.063	1.023	0.8787	0.671	0.5996	0.3292

1978	1.357	1.32	1.186	1.145	1.086	0.5018

1979	1.71	1.655	1.515	1.39	1.268	0.5621

1980	1.089	1.055	1.012	0.8784	0.8343	0.3913

1981	1.281	1.237	1.083	0.8581	0.7571	0.3527

1982	5.073	4.877	4.168	3.236	2.804	1.172

1983	1.419	1.371	1.264	1.108	0.9981	0.4348

1984	0.3464	0.3342	0.2898	0.2574	0.2501	0.179

1985	0.6526	0.627	0.5521	0.4792	0.4478	0.2562

1986	1.462	1.411	1.249	1.126	0.9797	0.4383

1987	0.8782	0.8472	0.7545	0.6033	0.5688	0.3157

1988	0.4931	0.4772	0.4254	0.3766	0.3514	0.2265

1989	0.3303	0.318	0.2735	0.2323	0.2258	0.1685

1990	0.5572	0.5378	0.4669	0.4006	0.3756	0.2349

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	5.073	4.877	4.168	3.236	2.804	1.172

0.0645161290322581	3.914	3.777	3.582	2.753	2.367	0.9559

0.0967741935483871	1.781	1.717	1.546	1.39	1.268	0.5621

0.129032258064516	1.759	1.699	1.515	1.341	1.187	0.5281

0.161290322580645	1.71	1.655	1.5	1.272	1.165	0.5039

0.193548387096774	1.628	1.589	1.388	1.145	1.086	0.5018

0.225806451612903	1.562	1.529	1.374	1.129	0.9981	0.4413

0.258064516129032	1.462	1.411	1.264	1.126	0.9797	0.4383

0.290322580645161	1.419	1.374	1.264	1.108	0.9753	0.4348

0.32258064516129	1.405	1.371	1.249	1.082	0.9418	0.4046

0.354838709677419	1.357	1.32	1.186	1.024	0.8713	0.4011

0.387096774193548	1.288	1.257	1.183	1.007	0.8675	0.3947

0.419354838709677	1.281	1.237	1.083	0.8829	0.8343	0.3913

0.451612903225806	1.234	1.193	1.06	0.8784	0.7864	0.3842

0.483870967741936	1.089	1.055	1.012	0.8581	0.7571	0.3527

0.516129032258065	1.063	1.023	0.8787	0.671	0.5996	0.3292

0.548387096774194	0.8782	0.8472	0.7545	0.6033	0.5688	0.3157

0.580645161290323	0.7903	0.7655	0.6905	0.5696	0.5511	0.2978

0.612903225806452	0.6929	0.6693	0.5862	0.4792	0.4481	0.2708

0.645161290322581	0.6526	0.627	0.5521	0.4708	0.4478	0.2562

0.67741935483871	0.604	0.582	0.523	0.4394	0.4065	0.2403

0.709677419354839	0.5824	0.5671	0.5065	0.415	0.38	0.2349

0.741935483870968	0.5572	0.5378	0.4669	0.4019	0.3756	0.2314

0.774193548387097	0.5404	0.5281	0.4654	0.4006	0.3696	0.2265

0.806451612903226	0.514	0.4982	0.4638	0.3766	0.3514	0.2223

0.838709677419355	0.4931	0.4772	0.4254	0.3742	0.3476	0.2211

0.870967741935484	0.4374	0.4227	0.3947	0.3497	0.3327	0.2185

0.903225806451613	0.3464	0.3342	0.2898	0.2574	0.2501	0.1846

0.935483870967742	0.3352	0.3234	0.2805	0.2556	0.2482	0.179

0.967741935483871	0.3303	0.318	0.2735	0.2323	0.2258	0.1685

0.1	1.7788	1.7152	1.5429	1.3851	1.2599	0.5587

					Average of yearly averages:	0.38212

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CAresidential

Metfile:	w23234.dvf

PRZM scenario:	CAresidential.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.5591	kg/ha

Application Efficiency:	APPEFF	0.99	fraction

Spray Drift	DRFT	0.01	fraction of application rate applied to pond

Application Date	Date	1-1	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval		days	Set to 0 or delete line for single app.

app. rate 1	apprate		kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

CA Cotton

stored as CACOTAIR.out

Chemical: DPXE2Y45

PRZM environment: CAcotton_WirrigSTD.txt	modified Tueday, 29 May 2007 at
12:42:12

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w93193.dvf	modified Wedday, 3 July 2002 at 09:04:24

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.527	0.506	0.4303	0.3275	0.2753	0.09387

1962	0.5664	0.5479	0.4758	0.3683	0.3059	0.1042

1963	1.04	1.001	0.9082	0.7729	0.6652	0.2561

1964	0.5514	0.5278	0.4462	0.3358	0.2783	0.09922

1965	2.888	2.774	2.37	1.79	1.464	0.5119

1966	0.5761	0.5549	0.4758	0.3581	0.2952	0.1081

1967	0.9171	0.8842	0.7675	0.607	0.5365	0.1948

1968	0.71	0.6859	0.5944	0.5486	0.4689	0.1644

1969	2.595	2.508	2.144	1.581	1.305	0.4404

1970	1.766	1.717	1.509	1.098	0.9047	0.3138

1971	0.6536	0.6282	0.537	0.4002	0.411	0.1705

1972	0.545	0.5242	0.4452	0.3273	0.2687	0.09284

1973	0.8286	0.8014	0.7123	0.5682	0.475	0.1637

1974	0.6707	0.6469	0.5602	0.4829	0.4135	0.1448

1975	0.5399	0.5199	0.4524	0.362	0.3051	0.1055

1976	0.5442	0.5238	0.4639	0.3495	0.2896	0.09897

1977	0.5343	0.5128	0.4349	0.3947	0.3389	0.1209

1978	1.128	1.088	0.9495	0.7247	0.6197	0.2163

1979	0.8605	0.8291	0.7376	0.5598	0.4631	0.158

1980	1.787	1.724	1.583	1.243	1.037	0.353

1981	0.556	0.536	0.4854	0.4094	0.3494	0.1238

1982	0.7089	0.6887	0.619	0.509	0.4401	0.1577

1983	1.021	0.9858	0.8637	0.6774	0.5693	0.1996

1984	0.5436	0.5222	0.4432	0.3276	0.2694	0.09201

1985	0.5329	0.511	0.4402	0.3438	0.2849	0.0962

1986	0.923	0.8938	0.8005	0.678	0.5814	0.2001

1987	1.113	1.074	0.9513	0.7165	0.606	0.2135

1988	0.8307	0.8038	0.6746	0.5419	0.509	0.1935

1989	1.382	1.329	1.139	1.017	0.8606	0.3063

1990	0.5509	0.5295	0.4521	0.3388	0.3163	0.1224

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	2.888	2.774	2.37	1.79	1.464	0.5119

0.0645161290322581	2.595	2.508	2.144	1.581	1.305	0.4404

0.0967741935483871	1.787	1.724	1.583	1.243	1.037	0.353

0.129032258064516	1.766	1.717	1.509	1.098	0.9047	0.3138

0.161290322580645	1.382	1.329	1.139	1.017	0.8606	0.3063

0.193548387096774	1.128	1.088	0.9513	0.7729	0.6652	0.2561

0.225806451612903	1.113	1.074	0.9495	0.7247	0.6197	0.2163

0.258064516129032	1.04	1.001	0.9082	0.7165	0.606	0.2135

0.290322580645161	1.021	0.9858	0.8637	0.678	0.5814	0.2001

0.32258064516129	0.923	0.8938	0.8005	0.6774	0.5693	0.1996

0.354838709677419	0.9171	0.8842	0.7675	0.607	0.5365	0.1948

0.387096774193548	0.8605	0.8291	0.7376	0.5682	0.509	0.1935

0.419354838709677	0.8307	0.8038	0.7123	0.5598	0.475	0.1705

0.451612903225806	0.8286	0.8014	0.6746	0.5486	0.4689	0.1644

0.483870967741936	0.71	0.6887	0.619	0.5419	0.4631	0.1637

0.516129032258065	0.7089	0.6859	0.5944	0.509	0.4401	0.158

0.548387096774194	0.6707	0.6469	0.5602	0.4829	0.4135	0.1577

0.580645161290323	0.6536	0.6282	0.537	0.4094	0.411	0.1448

0.612903225806452	0.5761	0.5549	0.4854	0.4002	0.3494	0.1238

0.645161290322581	0.5664	0.5479	0.4758	0.3947	0.3389	0.1224

0.67741935483871	0.556	0.536	0.4758	0.3683	0.3163	0.1209

0.709677419354839	0.5514	0.5295	0.4639	0.362	0.3059	0.1081

0.741935483870968	0.5509	0.5278	0.4524	0.3581	0.3051	0.1055

0.774193548387097	0.545	0.5242	0.4521	0.3495	0.2952	0.1042

0.806451612903226	0.5442	0.5238	0.4462	0.3438	0.2896	0.09922

0.838709677419355	0.5436	0.5222	0.4452	0.3388	0.2849	0.09897

0.870967741935484	0.5399	0.5199	0.4432	0.3358	0.2783	0.0962

0.903225806451613	0.5343	0.5128	0.4402	0.3276	0.2753	0.09387

0.935483870967742	0.5329	0.511	0.4349	0.3275	0.2694	0.09284

0.967741935483871	0.527	0.506	0.4303	0.3273	0.2687	0.09201

0.1	1.7849	1.7233	1.5756	1.2285	1.02377	0.34908

					Average of yearly averages:	0.187213666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CACOTAIR

Metfile:	w93193.dvf

PRZM scenario:	CAcotton_WirrigSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1109	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.05	fraction of application rate applied to pond

Application Date	Date	16-2	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	5	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1109	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

stored as CACOTGRD.out

Chemical: DPXE2Y45

PRZM environment: CAcotton_WirrigSTD.txt	modified Tueday, 29 May 2007 at
12:42:12

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w93193.dvf	modified Wedday, 3 July 2002 at 09:04:24

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.1054	0.1012	0.08607	0.0718	0.0655	0.02393

1962	0.1368	0.1327	0.1171	0.1008	0.0861	0.03001

1963	0.8479	0.815	0.7454	0.6182	0.5251	0.1855

1964	0.126	0.1209	0.1034	0.08048	0.06786	0.02735

1965	2.7	2.592	2.211	1.669	1.364	0.4545

1966	0.1497	0.1449	0.1268	0.09949	0.08396	0.0371

1967	0.6359	0.6124	0.53	0.4132	0.3423	0.1197

1968	0.4076	0.3972	0.3541	0.29	0.2567	0.09259

1969	2.273	2.196	1.877	1.374	1.132	0.3805

1970	1.477	1.417	1.256	0.9118	0.7409	0.2512

1971	0.5204	0.4989	0.4227	0.3094	0.2507	0.101

1972	0.1176	0.1133	0.09689	0.07229	0.05972	0.02249

1973	0.4626	0.4477	0.3989	0.316	0.2596	0.08877

1974	0.3286	0.3167	0.2734	0.2388	0.2003	0.0719

1975	0.1271	0.1228	0.1071	0.09393	0.08094	0.02919

1976	0.1336	0.1282	0.1132	0.08945	0.07504	0.02596

1977	0.2375	0.2282	0.208	0.1551	0.1324	0.04984

1978	0.8018	0.7724	0.6754	0.5125	0.4212	0.1429

1979	0.4451	0.4288	0.3942	0.3048	0.2508	0.08577

1980	1.41	1.381	1.283	1.015	0.8477	0.2884

1981	0.2124	0.2054	0.1785	0.147	0.1292	0.04983

1982	0.437	0.4253	0.3793	0.2809	0.2289	0.0825

1983	0.6704	0.6467	0.5661	0.432	0.3586	0.1241

1984	0.1161	0.1117	0.09529	0.07134	0.05899	0.02176

1985	0.1231	0.1184	0.1016	0.08643	0.07332	0.02529

1986	0.6333	0.6145	0.5594	0.4261	0.3734	0.1302

1987	0.8108	0.7792	0.6963	0.5203	0.4245	0.1456

1988	0.4923	0.478	0.4079	0.3461	0.3345	0.1285

1989	1.126	1.085	0.9277	0.8256	0.6988	0.2412

1990	0.2269	0.2179	0.1849	0.1336	0.1086	0.0518

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	2.7	2.592	2.211	1.669	1.364	0.4545

0.0645161290322581	2.273	2.196	1.877	1.374	1.132	0.3805

0.0967741935483871	1.477	1.417	1.283	1.015	0.8477	0.2884

0.129032258064516	1.41	1.381	1.256	0.9118	0.7409	0.2512

0.161290322580645	1.126	1.085	0.9277	0.8256	0.6988	0.2412

0.193548387096774	0.8479	0.815	0.7454	0.6182	0.5251	0.1855

0.225806451612903	0.8108	0.7792	0.6963	0.5203	0.4245	0.1456

0.258064516129032	0.8018	0.7724	0.6754	0.5125	0.4212	0.1429

0.290322580645161	0.6704	0.6467	0.5661	0.432	0.3734	0.1302

0.32258064516129	0.6359	0.6145	0.5594	0.4261	0.3586	0.1285

0.354838709677419	0.6333	0.6124	0.53	0.4132	0.3423	0.1241

0.387096774193548	0.5204	0.4989	0.4227	0.3461	0.3345	0.1197

0.419354838709677	0.4923	0.478	0.4079	0.316	0.2596	0.101

0.451612903225806	0.4626	0.4477	0.3989	0.3094	0.2567	0.09259

0.483870967741936	0.4451	0.4288	0.3942	0.3048	0.2508	0.08877

0.516129032258065	0.437	0.4253	0.3793	0.29	0.2507	0.08577

0.548387096774194	0.4076	0.3972	0.3541	0.2809	0.2289	0.0825

0.580645161290323	0.3286	0.3167	0.2734	0.2388	0.2003	0.0719

0.612903225806452	0.2375	0.2282	0.208	0.1551	0.1324	0.0518

0.645161290322581	0.2269	0.2179	0.1849	0.147	0.1292	0.04984

0.67741935483871	0.2124	0.2054	0.1785	0.1336	0.1086	0.04983

0.709677419354839	0.1497	0.1449	0.1268	0.1008	0.0861	0.0371

0.741935483870968	0.1368	0.1327	0.1171	0.09949	0.08396	0.03001

0.774193548387097	0.1336	0.1282	0.1132	0.09393	0.08094	0.02919

0.806451612903226	0.1271	0.1228	0.1071	0.08945	0.07504	0.02735

0.838709677419355	0.126	0.1209	0.1034	0.08643	0.07332	0.02596

0.870967741935484	0.1231	0.1184	0.1016	0.08048	0.06786	0.02529

0.903225806451613	0.1176	0.1133	0.09689	0.07229	0.0655	0.02393

0.935483870967742	0.1161	0.1117	0.09529	0.0718	0.05972	0.02249

0.967741935483871	0.1054	0.1012	0.08607	0.07134	0.05899	0.02176

0.1	1.4703	1.4134	1.2803	1.00468	0.83702	0.28468

					Average of yearly averages:	0.116979333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CACOTGRD

Metfile:	w93193.dvf

PRZM scenario:	CAcotton_WirrigSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1109	kg/ha

Application Efficiency:	APPEFF	0.99	fraction

Spray Drift	DRFT	0.01	fraction of application rate applied to pond

Application Date	Date	16-2	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	5	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1109	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

CA Grape

stored as CAGRAPAIR.out

Chemical: DPXE2Y45

PRZM environment: CAgrapes_WirrigSTD.txt	modified Tueday, 29 May 2007 at
12:42:54

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w93193.dvf	modified Wedday, 3 July 2002 at 09:04:24

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.5171	0.4966	0.4228	0.3191	0.2657	0.09045

1962	1.361	1.32	1.168	0.8733	0.7171	0.2461

1963	0.7761	0.7483	0.676	0.5199	0.4457	0.1641

1964	0.529	0.5062	0.4257	0.321	0.2671	0.09333

1965	0.9447	0.9087	0.779	0.584	0.5202	0.2006

1966	0.5369	0.5166	0.4432	0.3354	0.2784	0.09653

1967	0.527	0.5078	0.4382	0.3538	0.3202	0.1209

1968	0.5319	0.5139	0.4481	0.3468	0.2935	0.102

1969	0.939	0.9083	0.78	0.6087	0.5194	0.1856

1970	0.6396	0.6175	0.5325	0.4526	0.3905	0.1395

1971	0.5285	0.5081	0.4346	0.327	0.273	0.09609

1972	0.5255	0.5052	0.4322	0.3229	0.2668	0.091

1973	0.9266	0.8949	0.7789	0.6029	0.5039	0.1763

1974	0.5318	0.5111	0.4364	0.335	0.2851	0.09971

1975	0.5264	0.5068	0.4359	0.3342	0.282	0.09792

1976	1.318	1.268	1.089	0.7993	0.6576	0.2272

1977	0.5345	0.5133	0.4413	0.3372	0.2808	0.09872

1978	1.195	1.167	1.035	0.8016	0.6729	0.2341

1979	0.5378	0.5184	0.4678	0.3681	0.3111	0.1086

1980	1.122	1.083	0.9424	0.7142	0.6064	0.2162

1981	0.5369	0.5175	0.447	0.356	0.3087	0.1096

1982	0.5274	0.5077	0.4365	0.3619	0.319	0.1153

1983	0.6622	0.6392	0.5555	0.464	0.3976	0.1414

1984	0.5286	0.5129	0.4384	0.3282	0.272	0.09254

1985	0.5308	0.5092	0.4314	0.3253	0.2707	0.09205

1986	1.059	1.02	0.8818	0.6783	0.5665	0.1971

1987	0.5341	0.5139	0.4713	0.3606	0.302	0.1049

1988	0.5217	0.4995	0.4206	0.3255	0.2722	0.09441

1989	0.5264	0.5073	0.4377	0.3474	0.2996	0.1049

1990	0.538	0.5168	0.4405	0.3316	0.2759	0.09468

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	1.361	1.32	1.168	0.8733	0.7171	0.2461

0.0645161290322581	1.318	1.268	1.089	0.8016	0.6729	0.2341

0.0967741935483871	1.195	1.167	1.035	0.7993	0.6576	0.2272

0.129032258064516	1.122	1.083	0.9424	0.7142	0.6064	0.2162

0.161290322580645	1.059	1.02	0.8818	0.6783	0.5665	0.2006

0.193548387096774	0.9447	0.9087	0.78	0.6087	0.5202	0.1971

0.225806451612903	0.939	0.9083	0.779	0.6029	0.5194	0.1856

0.258064516129032	0.9266	0.8949	0.7789	0.584	0.5039	0.1763

0.290322580645161	0.7761	0.7483	0.676	0.5199	0.4457	0.1641

0.32258064516129	0.6622	0.6392	0.5555	0.464	0.3976	0.1414

0.354838709677419	0.6396	0.6175	0.5325	0.4526	0.3905	0.1395

0.387096774193548	0.538	0.5184	0.4713	0.3681	0.3202	0.1209

0.419354838709677	0.5378	0.5175	0.4678	0.3619	0.319	0.1153

0.451612903225806	0.5369	0.5168	0.4481	0.3606	0.3111	0.1096

0.483870967741936	0.5369	0.5166	0.447	0.356	0.3087	0.1086

0.516129032258065	0.5345	0.5139	0.4432	0.3538	0.302	0.1049

0.548387096774194	0.5341	0.5139	0.4413	0.3474	0.2996	0.1049

0.580645161290323	0.5319	0.5133	0.4405	0.3468	0.2935	0.102

0.612903225806452	0.5318	0.5129	0.4384	0.3372	0.2851	0.09971

0.645161290322581	0.5308	0.5111	0.4382	0.3354	0.282	0.09872

0.67741935483871	0.529	0.5092	0.4377	0.335	0.2808	0.09792

0.709677419354839	0.5286	0.5081	0.4365	0.3342	0.2784	0.09653

0.741935483870968	0.5285	0.5078	0.4364	0.3316	0.2759	0.09609

0.774193548387097	0.5274	0.5077	0.4359	0.3282	0.273	0.09468

0.806451612903226	0.527	0.5073	0.4346	0.327	0.2722	0.09441

0.838709677419355	0.5264	0.5068	0.4322	0.3255	0.272	0.09333

0.870967741935484	0.5264	0.5062	0.4314	0.3253	0.2707	0.09254

0.903225806451613	0.5255	0.5052	0.4257	0.3229	0.2671	0.09205

0.935483870967742	0.5217	0.4995	0.4228	0.321	0.2668	0.091

0.967741935483871	0.5171	0.4966	0.4206	0.3191	0.2657	0.09045

0.1	1.1877	1.1586	1.02574	0.79079	0.65248	0.2261

					Average of yearly averages:	0.134394333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CAGRAPAIR

Metfile:	w93193.dvf

PRZM scenario:	CAgrapes_WirrigSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1109	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.05	fraction of application rate applied to pond

Application Date	Date	1-2	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	7	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1109	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

stored as CAGRAPGRD.out

Chemical: DPXE2Y45

PRZM environment: CAgrapes_WirrigSTD.txt	modified Tueday, 29 May 2007 at
12:42:54

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w93193.dvf	modified Wedday, 3 July 2002 at 09:04:24

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.1034	0.09932	0.08456	0.06478	0.05474	0.01885

1962	0.9943	0.9627	0.8516	0.6331	0.5173	0.174

1963	0.3897	0.376	0.3411	0.2688	0.2347	0.08744

1964	0.1113	0.1067	0.09059	0.07059	0.05928	0.02158

1965	0.7439	0.7144	0.6086	0.4512	0.3683	0.1295

1966	0.1171	0.1129	0.09755	0.07514	0.06285	0.02316

1967	0.1292	0.1251	0.1144	0.106	0.09732	0.04123

1968	0.1084	0.1048	0.09161	0.07522	0.06652	0.02421

1969	0.6358	0.6143	0.5253	0.3853	0.3181	0.1112

1970	0.3651	0.3534	0.3059	0.2226	0.1821	0.06729

1971	0.1092	0.1051	0.09016	0.06832	0.05838	0.02184

1972	0.1054	0.1014	0.08673	0.06504	0.05393	0.01853

1973	0.543	0.5241	0.4553	0.3491	0.289	0.09917

1974	0.1118	0.1076	0.09228	0.07264	0.06491	0.02413

1975	0.1057	0.1018	0.08757	0.0675	0.05707	0.01991

1976	0.9393	0.9037	0.7748	0.5656	0.4627	0.1575

1977	0.116	0.1116	0.1002	0.0815	0.06917	0.02575

1978	0.8144	0.8	0.7097	0.5549	0.4653	0.1588

1979	0.1474	0.1424	0.1239	0.1024	0.08789	0.03217

1980	0.8037	0.775	0.6743	0.5031	0.4135	0.1432

1981	0.125	0.1209	0.1054	0.09219	0.08497	0.0331

1982	0.1476	0.1429	0.1308	0.1023	0.09557	0.0372

1983	0.2541	0.2458	0.2164	0.198	0.1712	0.06133

1984	0.1139	0.1098	0.09503	0.07144	0.05955	0.02072

1985	0.1132	0.1086	0.09202	0.07014	0.05887	0.02018

1986	0.693	0.6671	0.5767	0.4449	0.3681	0.1251

1987	0.1568	0.151	0.1298	0.1022	0.08649	0.03116

1988	0.1095	0.1049	0.08898	0.07897	0.06869	0.02485

1989	0.1059	0.102	0.08809	0.08526	0.07785	0.02919

1990	0.1199	0.1152	0.09826	0.07422	0.06195	0.02158

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	0.9943	0.9627	0.8516	0.6331	0.5173	0.174

0.0645161290322581	0.9393	0.9037	0.7748	0.5656	0.4653	0.1588

0.0967741935483871	0.8144	0.8	0.7097	0.5549	0.4627	0.1575

0.129032258064516	0.8037	0.775	0.6743	0.5031	0.4135	0.1432

0.161290322580645	0.7439	0.7144	0.6086	0.4512	0.3683	0.1295

0.193548387096774	0.693	0.6671	0.5767	0.4449	0.3681	0.1251

0.225806451612903	0.6358	0.6143	0.5253	0.3853	0.3181	0.1112

0.258064516129032	0.543	0.5241	0.4553	0.3491	0.289	0.09917

0.290322580645161	0.3897	0.376	0.3411	0.2688	0.2347	0.08744

0.32258064516129	0.3651	0.3534	0.3059	0.2226	0.1821	0.06729

0.354838709677419	0.2541	0.2458	0.2164	0.198	0.1712	0.06133

0.387096774193548	0.1568	0.151	0.1308	0.106	0.09732	0.04123

0.419354838709677	0.1476	0.1429	0.1298	0.1024	0.09557	0.0372

0.451612903225806	0.1474	0.1424	0.1239	0.1023	0.08789	0.0331

0.483870967741936	0.1292	0.1251	0.1144	0.1022	0.08649	0.03217

0.516129032258065	0.125	0.1209	0.1054	0.09219	0.08497	0.03116

0.548387096774194	0.1199	0.1152	0.1002	0.08526	0.07785	0.02919

0.580645161290323	0.1171	0.1129	0.09826	0.0815	0.06917	0.02575

0.612903225806452	0.116	0.1116	0.09755	0.07897	0.06869	0.02485

0.645161290322581	0.1139	0.1098	0.09503	0.07522	0.06652	0.02421

0.67741935483871	0.1132	0.1086	0.09228	0.07514	0.06491	0.02413

0.709677419354839	0.1118	0.1076	0.09202	0.07422	0.06285	0.02316

0.741935483870968	0.1113	0.1067	0.09161	0.07264	0.06195	0.02184

0.774193548387097	0.1095	0.1051	0.09059	0.07144	0.05955	0.02158

0.806451612903226	0.1092	0.1049	0.09016	0.07059	0.05928	0.02158

0.838709677419355	0.1084	0.1048	0.08898	0.07014	0.05887	0.02072

0.870967741935484	0.1059	0.102	0.08809	0.06832	0.05838	0.02018

0.903225806451613	0.1057	0.1018	0.08757	0.0675	0.05707	0.01991

0.935483870967742	0.1054	0.1014	0.08673	0.06504	0.05474	0.01885

0.967741935483871	0.1034	0.09932	0.08456	0.06478	0.05393	0.01853

0.1	0.81333	0.7975	0.70616	0.54972	0.45778	0.15607

					Average of yearly averages:	0.060129

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CAGRAPGRD

Metfile:	w93193.dvf

PRZM scenario:	CAgrapes_WirrigSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1109	kg/ha

Application Efficiency:	APPEFF	0.99	fraction

Spray Drift	DRFT	0.01	fraction of application rate applied to pond

Application Date	Date	1-2	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	7	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1109	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

CA Lettuce

stored as CALETAIR.out

Chemical: DPXE2Y45

PRZM environment: CAlettuceSTD.txt	modified Tueday, 21 February 2006 at
14:38:22

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w23273.dvf	modified Wedday, 3 July 2002 at 09:04:22

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	1.977	1.918	1.641	1.011	0.6815	0.2533

1962	1.971	1.909	1.722	1.352	1.207	0.5421

1963	2.49	2.393	2.191	1.805	1.535	0.6179

1964	0.8977	0.864	0.7851	0.6179	0.557	0.2997

1965	0.8491	0.8213	0.7284	0.57	0.5516	0.264

1966	1.336	1.283	1.114	0.8178	0.555	0.2434

1967	0.9966	0.9629	0.8842	0.8193	0.763	0.3745

1968	1.086	1.044	0.9011	0.6981	0.614	0.2889

1969	3.597	3.464	3.012	2.203	1.821	0.6793

1970	4.304	4.123	3.68	2.663	2.162	0.8057

1971	0.7059	0.682	0.5902	0.4532	0.4033	0.268

1972	1.527	1.469	1.275	0.9252	0.6943	0.2896

1973	1.287	1.244	1.151	1.013	0.8807	0.408

1974	3.971	3.84	3.423	2.621	2.162	0.7964

1975	1.64	1.579	1.362	1.02	0.8678	0.3528

1976	0.855	0.8208	0.6979	0.5678	0.502	0.3292

1977	1.509	1.446	1.223	0.9779	0.9656	0.4509

1978	3.038	2.926	2.565	1.94	1.618	0.6222

1979	1.474	1.417	1.231	1.016	0.86	0.3235

1980	1.828	1.759	1.613	1.279	1.067	0.398

1981	3.37	3.267	2.861	2.203	1.829	0.6772

1982	0.8822	0.8507	0.7991	0.659	0.5925	0.2482

1983	2.214	2.139	1.891	1.457	1.212	0.4408

1984	0.5706	0.55	0.486	0.3694	0.3024	0.1725

1985	0.715	0.6882	0.6244	0.5076	0.4318	0.2534

1986	2.047	1.974	1.754	1.399	1.167	0.4756

1987	3.416	3.294	2.813	2.058	1.692	0.6385

1988	2.088	1.997	1.668	1.248	1.098	0.437

1989	0.5816	0.5607	0.486	0.3728	0.3122	0.1368

1990	0.7601	0.7309	0.6365	0.4911	0.4105	0.1818

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	4.304	4.123	3.68	2.663	2.162	0.8057

0.0645161290322581	3.971	3.84	3.423	2.621	2.162	0.7964

0.0967741935483871	3.597	3.464	3.012	2.203	1.829	0.6793

0.129032258064516	3.416	3.294	2.861	2.203	1.821	0.6772

0.161290322580645	3.37	3.267	2.813	2.058	1.692	0.6385

0.193548387096774	3.038	2.926	2.565	1.94	1.618	0.6222

0.225806451612903	2.49	2.393	2.191	1.805	1.535	0.6179

0.258064516129032	2.214	2.139	1.891	1.457	1.212	0.5421

0.290322580645161	2.088	1.997	1.754	1.399	1.207	0.4756

0.32258064516129	2.047	1.974	1.722	1.352	1.167	0.4509

0.354838709677419	1.977	1.918	1.668	1.279	1.098	0.4408

0.387096774193548	1.971	1.909	1.641	1.248	1.067	0.437

0.419354838709677	1.828	1.759	1.613	1.02	0.9656	0.408

0.451612903225806	1.64	1.579	1.362	1.016	0.8807	0.398

0.483870967741936	1.527	1.469	1.275	1.013	0.8678	0.3745

0.516129032258065	1.509	1.446	1.231	1.011	0.86	0.3528

0.548387096774194	1.474	1.417	1.223	0.9779	0.763	0.3292

0.580645161290323	1.336	1.283	1.151	0.9252	0.6943	0.3235

0.612903225806452	1.287	1.244	1.114	0.8193	0.6815	0.2997

0.645161290322581	1.086	1.044	0.9011	0.8178	0.614	0.2896

0.67741935483871	0.9966	0.9629	0.8842	0.6981	0.5925	0.2889

0.709677419354839	0.8977	0.864	0.7991	0.659	0.557	0.268

0.741935483870968	0.8822	0.8507	0.7851	0.6179	0.555	0.264

0.774193548387097	0.855	0.8213	0.7284	0.57	0.5516	0.2534

0.806451612903226	0.8491	0.8208	0.6979	0.5678	0.502	0.2533

0.838709677419355	0.7601	0.7309	0.6365	0.5076	0.4318	0.2482

0.870967741935484	0.715	0.6882	0.6244	0.4911	0.4105	0.2434

0.903225806451613	0.7059	0.682	0.5902	0.4532	0.4033	0.1818

0.935483870967742	0.5816	0.5607	0.486	0.3728	0.3122	0.1725

0.967741935483871	0.5706	0.55	0.486	0.3694	0.3024	0.1368

0.1	3.5789	3.447	2.9969	2.203	1.8282	0.67909

					Average of yearly averages:	0.408973333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CALETAIR

Metfile:	w23273.dvf

PRZM scenario:	CAlettuceSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.0728	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.05	fraction of application rate applied to pond

Application Date	Date	16-2	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	3	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.0728	kg/ha

Interval 2	interval	3	days	Set to 0 or delete line for single app.

app. rate 2	apprate	0.0728	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

stored as CALETGRD.out

Chemical: DPXE2Y45

PRZM environment: CAlettuceSTD.txt	modified Tueday, 21 February 2006 at
14:38:22

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w23273.dvf	modified Wedday, 3 July 2002 at 09:04:22

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	2.049	1.987	1.699	1.041	0.6957	0.1896

1962	1.627	1.595	1.43	1.159	1.1	0.4827

1963	2.365	2.272	2.046	1.701	1.446	0.5613

1964	0.7311	0.7028	0.6176	0.4908	0.4108	0.2346

1965	0.6878	0.6645	0.5862	0.4449	0.3777	0.1906

1966	1.378	1.323	1.147	0.8372	0.5611	0.1717

1967	0.8345	0.8063	0.7031	0.6576	0.6375	0.3064

1968	0.8235	0.7915	0.682	0.5217	0.4323	0.2187

1969	3.323	3.201	2.792	2.042	1.685	0.6278

1970	4.128	3.954	3.519	2.547	2.067	0.7627

1971	0.6414	0.6187	0.5318	0.3943	0.3257	0.2001

1972	1.575	1.515	1.313	0.95	0.7072	0.2232

1973	1.036	1.007	0.9023	0.797	0.6897	0.3428

1974	3.762	3.638	3.251	2.493	2.057	0.7475

1975	1.367	1.315	1.135	0.8495	0.7046	0.2846

1976	0.83	0.8048	0.693	0.5594	0.4961	0.2639

1977	1.302	1.26	1.089	0.8519	0.8669	0.3937

1978	2.801	2.698	2.368	1.79	1.482	0.5654

1979	1.096	1.054	0.9213	0.7858	0.6723	0.2558

1980	1.464	1.434	1.321	1.064	0.8889	0.3346

1981	3.158	3.057	2.678	2.059	1.702	0.6245

1982	0.6891	0.666	0.5989	0.5069	0.4308	0.1771

1983	1.925	1.855	1.639	1.255	1.045	0.3737

1984	0.5841	0.5628	0.4961	0.3729	0.2601	0.104

1985	0.5222	0.5022	0.4547	0.3469	0.3006	0.1837

1986	1.839	1.773	1.566	1.244	1.039	0.4129

1987	3.207	3.094	2.64	1.929	1.584	0.5842

1988	1.801	1.723	1.438	1.084	0.9592	0.3801

1989	0.1661	0.1609	0.1456	0.1169	0.1079	0.06223

1990	0.3537	0.3408	0.3118	0.2604	0.239	0.109

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	4.128	3.954	3.519	2.547	2.067	0.7627

0.0645161290322581	3.762	3.638	3.251	2.493	2.057	0.7475

0.0967741935483871	3.323	3.201	2.792	2.059	1.702	0.6278

0.129032258064516	3.207	3.094	2.678	2.042	1.685	0.6245

0.161290322580645	3.158	3.057	2.64	1.929	1.584	0.5842

0.193548387096774	2.801	2.698	2.368	1.79	1.482	0.5654

0.225806451612903	2.365	2.272	2.046	1.701	1.446	0.5613

0.258064516129032	2.049	1.987	1.699	1.255	1.1	0.4827

0.290322580645161	1.925	1.855	1.639	1.244	1.045	0.4129

0.32258064516129	1.839	1.773	1.566	1.159	1.039	0.3937

0.354838709677419	1.801	1.723	1.438	1.084	0.9592	0.3801

0.387096774193548	1.627	1.595	1.43	1.064	0.8889	0.3737

0.419354838709677	1.575	1.515	1.321	1.041	0.8669	0.3428

0.451612903225806	1.464	1.434	1.313	0.95	0.7072	0.3346

0.483870967741936	1.378	1.323	1.147	0.8519	0.7046	0.3064

0.516129032258065	1.367	1.315	1.135	0.8495	0.6957	0.2846

0.548387096774194	1.302	1.26	1.089	0.8372	0.6897	0.2639

0.580645161290323	1.096	1.054	0.9213	0.797	0.6723	0.2558

0.612903225806452	1.036	1.007	0.9023	0.7858	0.6375	0.2346

0.645161290322581	0.8345	0.8063	0.7031	0.6576	0.5611	0.2232

0.67741935483871	0.83	0.8048	0.693	0.5594	0.4961	0.2187

0.709677419354839	0.8235	0.7915	0.682	0.5217	0.4323	0.2001

0.741935483870968	0.7311	0.7028	0.6176	0.5069	0.4308	0.1906

0.774193548387097	0.6891	0.666	0.5989	0.4908	0.4108	0.1896

0.806451612903226	0.6878	0.6645	0.5862	0.4449	0.3777	0.1837

0.838709677419355	0.6414	0.6187	0.5318	0.3943	0.3257	0.1771

0.870967741935484	0.5841	0.5628	0.4961	0.3729	0.3006	0.1717

0.903225806451613	0.5222	0.5022	0.4547	0.3469	0.2601	0.109

0.935483870967742	0.3537	0.3408	0.3118	0.2604	0.239	0.104

0.967741935483871	0.1661	0.1609	0.1456	0.1169	0.1079	0.06223

0.1	3.3114	3.1903	2.7806	2.0573	1.7003	0.62747

					Average of yearly averages:	0.345637666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CALETGRD

Metfile:	w23273.dvf

PRZM scenario:	CAlettuceSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.0728	kg/ha

Application Efficiency:	APPEFF	0.99	fraction

Spray Drift	DRFT	0.01	fraction of application rate applied to pond

Application Date	Date	16-2	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	3	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.0728	kg/ha

Interval 2	interval	3	days	Set to 0 or delete line for single app.

app. rate 2	apprate	0.0728	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

CA Tomato

stored as CATOMAIR.out

Chemical: DPXE2Y45

PRZM environment: CAtomato_WirrigSTD.txt	modified Tueday, 29 May 2007 at
12:43:54

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w93193.dvf	modified Wedday, 3 July 2002 at 09:04:24

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.5216	0.5007	0.4283	0.3209	0.2639	0.08737

1962	0.5291	0.5082	0.4439	0.3419	0.2825	0.09535

1963	0.7165	0.6896	0.6333	0.5658	0.4951	0.179

1964	0.5382	0.5168	0.4407	0.3285	0.2707	0.09458

1965	2.011	1.931	1.648	1.237	1.014	0.3468

1966	0.5505	0.5285	0.4499	0.3341	0.274	0.09759

1967	0.8163	0.7864	0.6849	0.5703	0.484	0.1691

1968	0.7195	0.6943	0.6039	0.4846	0.4053	0.1397

1969	0.6117	0.5872	0.5136	0.447	0.3822	0.1344

1970	1.133	1.086	0.938	0.7028	0.5725	0.1898

1971	0.5343	0.5124	0.4598	0.3493	0.2943	0.1032

1972	0.5273	0.5042	0.423	0.3107	0.2541	0.08587

1973	0.6907	0.6673	0.5775	0.4681	0.3935	0.135

1974	0.5813	0.56	0.483	0.3975	0.3328	0.1136

1975	0.5326	0.5131	0.4645	0.3548	0.2944	0.09991

1976	0.5303	0.5084	0.4299	0.3189	0.262	0.0888

1977	0.5279	0.5063	0.4714	0.3638	0.3021	0.1035

1978	0.8467	0.8185	0.7138	0.6387	0.5434	0.1869

1979	0.5623	0.5414	0.4854	0.3781	0.3129	0.107

1980	1.079	1.036	0.8806	0.6416	0.528	0.1781

1981	0.6689	0.6451	0.5563	0.4561	0.3845	0.1321

1982	0.8655	0.8461	0.7656	0.6014	0.5022	0.1747

1983	0.9613	0.929	0.8814	0.7307	0.6131	0.2104

1984	0.5366	0.514	0.4344	0.3216	0.2635	0.09011

1985	0.5283	0.5074	0.4409	0.3271	0.2676	0.08931

1986	1.08	1.039	0.9267	0.7012	0.5778	0.1948

1987	0.7124	0.6848	0.6154	0.4735	0.3926	0.1344

1988	0.5282	0.5047	0.4212	0.3171	0.2667	0.0918

1989	0.7747	0.7465	0.6379	0.5678	0.4791	0.1629

1990	0.533	0.5116	0.4346	0.3238	0.2677	0.09148

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	2.011	1.931	1.648	1.237	1.014	0.3468

0.0645161290322581	1.133	1.086	0.938	0.7307	0.6131	0.2104

0.0967741935483871	1.08	1.039	0.9267	0.7028	0.5778	0.1948

0.129032258064516	1.079	1.036	0.8814	0.7012	0.5725	0.1898

0.161290322580645	0.9613	0.929	0.8806	0.6416	0.5434	0.1869

0.193548387096774	0.8655	0.8461	0.7656	0.6387	0.528	0.179

0.225806451612903	0.8467	0.8185	0.7138	0.6014	0.5022	0.1781

0.258064516129032	0.8163	0.7864	0.6849	0.5703	0.4951	0.1747

0.290322580645161	0.7747	0.7465	0.6379	0.5678	0.484	0.1691

0.32258064516129	0.7195	0.6943	0.6333	0.5658	0.4791	0.1629

0.354838709677419	0.7165	0.6896	0.6154	0.4846	0.4053	0.1397

0.387096774193548	0.7124	0.6848	0.6039	0.4735	0.3935	0.135

0.419354838709677	0.6907	0.6673	0.5775	0.4681	0.3926	0.1344

0.451612903225806	0.6689	0.6451	0.5563	0.4561	0.3845	0.1344

0.483870967741936	0.6117	0.5872	0.5136	0.447	0.3822	0.1321

0.516129032258065	0.5813	0.56	0.4854	0.3975	0.3328	0.1136

0.548387096774194	0.5623	0.5414	0.483	0.3781	0.3129	0.107

0.580645161290323	0.5505	0.5285	0.4714	0.3638	0.3021	0.1035

0.612903225806452	0.5382	0.5168	0.4645	0.3548	0.2944	0.1032

0.645161290322581	0.5366	0.514	0.4598	0.3493	0.2943	0.09991

0.67741935483871	0.5343	0.5131	0.4499	0.3419	0.2825	0.09759

0.709677419354839	0.533	0.5124	0.4439	0.3341	0.274	0.09535

0.741935483870968	0.5326	0.5116	0.4409	0.3285	0.2707	0.09458

0.774193548387097	0.5303	0.5084	0.4407	0.3271	0.2677	0.0918

0.806451612903226	0.5291	0.5082	0.4346	0.3238	0.2676	0.09148

0.838709677419355	0.5283	0.5074	0.4344	0.3216	0.2667	0.09011

0.870967741935484	0.5282	0.5063	0.4299	0.3209	0.2639	0.08931

0.903225806451613	0.5279	0.5047	0.4283	0.3189	0.2635	0.0888

0.935483870967742	0.5273	0.5042	0.423	0.3171	0.262	0.08737

0.967741935483871	0.5216	0.5007	0.4212	0.3107	0.2541	0.08587

0.1	1.0799	1.0387	0.92217	0.70264	0.57727	0.1943

					Average of yearly averages:	0.136919

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CATOMAIR

Metfile:	w93193.dvf

PRZM scenario:	CAtomato_WirrigSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1098	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.05	fraction of application rate applied to pond

Application Date	Date	1-3	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	5	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1098	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

stored as CATOMGRD.out

Chemical: DPXE2Y45

PRZM environment: CAtomato_WirrigSTD.txt	modified Tueday, 29 May 2007 at
12:43:54

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w93193.dvf	modified Wedday, 3 July 2002 at 09:04:24

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.1043	0.1001	0.08797	0.06987	0.05825	0.01951

1962	0.1285	0.1236	0.1052	0.08715	0.0736	0.02528

1963	0.4573	0.4395	0.4167	0.352	0.3027	0.1079

1964	0.1151	0.1107	0.09566	0.07252	0.06018	0.02302

1965	1.701	1.633	1.392	1.046	0.8545	0.2838

1966	0.1289	0.1241	0.1074	0.08226	0.06831	0.02879

1967	0.4518	0.435	0.381	0.3263	0.2748	0.09517

1968	0.3624	0.3509	0.3103	0.2464	0.2032	0.07117

1969	0.3248	0.3115	0.2641	0.2068	0.181	0.06597

1970	0.7371	0.7094	0.6368	0.4669	0.3792	0.125

1971	0.1447	0.1389	0.1198	0.0998	0.08748	0.03309

1972	0.1066	0.102	0.0863	0.06391	0.05238	0.01808

1973	0.3691	0.3562	0.3067	0.2204	0.1804	0.06249

1974	0.185	0.1811	0.1593	0.1361	0.1167	0.04125

1975	0.1342	0.1294	0.113	0.0892	0.07471	0.02582

1976	0.1087	0.1042	0.08815	0.06551	0.05385	0.01838

1977	0.1752	0.1681	0.1511	0.115	0.09637	0.03352

1978	0.4866	0.4697	0.4387	0.3855	0.3355	0.1158

1979	0.1578	0.1522	0.1393	0.1177	0.09928	0.03562

1980	0.6797	0.6524	0.5541	0.4031	0.3291	0.1097

1981	0.3459	0.3333	0.2863	0.2093	0.1739	0.06147

1982	0.5298	0.5188	0.4703	0.3637	0.2969	0.1026

1983	0.6055	0.5855	0.5683	0.4755	0.4017	0.1384

1984	0.1152	0.1105	0.09504	0.07174	0.0592	0.02223

1985	0.11	0.1057	0.09604	0.07189	0.05903	0.0198

1986	0.7505	0.7219	0.6249	0.4737	0.3862	0.1274

1987	0.317	0.3053	0.2761	0.2274	0.1881	0.06547

1988	0.1087	0.1039	0.08693	0.07114	0.06358	0.02354

1989	0.4968	0.4783	0.4073	0.3199	0.276	0.09481

1990	0.1114	0.1071	0.09147	0.06944	0.05873	0.02164

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	1.701	1.633	1.392	1.046	0.8545	0.2838

0.0645161290322581	0.7505	0.7219	0.6368	0.4755	0.4017	0.1384

0.0967741935483871	0.7371	0.7094	0.6249	0.4737	0.3862	0.1274

0.129032258064516	0.6797	0.6524	0.5683	0.4669	0.3792	0.125

0.161290322580645	0.6055	0.5855	0.5541	0.4031	0.3355	0.1158

0.193548387096774	0.5298	0.5188	0.4703	0.3855	0.3291	0.1097

0.225806451612903	0.4968	0.4783	0.4387	0.3637	0.3027	0.1079

0.258064516129032	0.4866	0.4697	0.4167	0.352	0.2969	0.1026

0.290322580645161	0.4573	0.4395	0.4073	0.3263	0.276	0.09517

0.32258064516129	0.4518	0.435	0.381	0.3199	0.2748	0.09481

0.354838709677419	0.3691	0.3562	0.3103	0.2464	0.2032	0.07117

0.387096774193548	0.3624	0.3509	0.3067	0.2274	0.1881	0.06597

0.419354838709677	0.3459	0.3333	0.2863	0.2204	0.181	0.06547

0.451612903225806	0.3248	0.3115	0.2761	0.2093	0.1804	0.06249

0.483870967741936	0.317	0.3053	0.2641	0.2068	0.1739	0.06147

0.516129032258065	0.185	0.1811	0.1593	0.1361	0.1167	0.04125

0.548387096774194	0.1752	0.1681	0.1511	0.1177	0.09928	0.03562

0.580645161290323	0.1578	0.1522	0.1393	0.115	0.09637	0.03352

0.612903225806452	0.1447	0.1389	0.1198	0.0998	0.08748	0.03309

0.645161290322581	0.1342	0.1294	0.113	0.0892	0.07471	0.02879

0.67741935483871	0.1289	0.1241	0.1074	0.08715	0.0736	0.02582

0.709677419354839	0.1285	0.1236	0.1052	0.08226	0.06831	0.02528

0.741935483870968	0.1152	0.1107	0.09604	0.07252	0.06358	0.02354

0.774193548387097	0.1151	0.1105	0.09566	0.07189	0.06018	0.02302

0.806451612903226	0.1114	0.1071	0.09504	0.07174	0.0592	0.02223

0.838709677419355	0.11	0.1057	0.09147	0.07114	0.05903	0.02164

0.870967741935484	0.1087	0.1042	0.08815	0.06987	0.05873	0.0198

0.903225806451613	0.1087	0.1039	0.08797	0.06944	0.05825	0.01951

0.935483870967742	0.1066	0.102	0.08693	0.06551	0.05385	0.01838

0.967741935483871	0.1043	0.1001	0.0863	0.06391	0.05238	0.01808

0.1	0.73136	0.7037	0.61924	0.47302	0.3855	0.12716

					Average of yearly averages:	0.067224

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CATOMGRD

Metfile:	w93193.dvf

PRZM scenario:	CAtomato_WirrigSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1098	kg/ha

Application Efficiency:	APPEFF	0.99	fraction

Spray Drift	DRFT	0.01	fraction of application rate applied to pond

Application Date	Date	1-3	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	5	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1098	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

CA Turf

stored as CATURFGRD.out

Chemical: DPXE2Y45

PRZM environment: CATurfRLF.txt	modified Tueday, 20 February 2007 at
12:03:48

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w23234.dvf	modified Wedday, 3 July 2002 at 09:04:22

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.2703	0.2588	0.2394	0.193	0.1656	0.06767

1962	0.6401	0.6158	0.5279	0.3945	0.3238	0.1582

1963	0.4295	0.416	0.3885	0.3141	0.2704	0.1458

1964	0.3227	0.3102	0.2655	0.2072	0.1782	0.09411

1965	0.5031	0.4856	0.4219	0.3171	0.2665	0.1155

1966	0.3178	0.3057	0.262	0.2029	0.1706	0.09447

1967	0.7069	0.6908	0.6217	0.4831	0.4179	0.2076

1968	0.3342	0.3209	0.2736	0.2142	0.184	0.0964

1969	0.354	0.3408	0.2942	0.2297	0.1967	0.1057

1970	0.3121	0.3005	0.2587	0.2046	0.1771	0.09475

1971	0.3008	0.2924	0.2536	0.1974	0.1713	0.08037

1972	0.2814	0.2713	0.2338	0.1876	0.1622	0.09582

1973	0.3263	0.3134	0.2696	0.2101	0.1789	0.1039

1974	0.4784	0.4602	0.3984	0.3132	0.261	0.1166

1975	0.3493	0.3369	0.2921	0.2322	0.2012	0.09315

1976	0.2995	0.288	0.2467	0.19	0.1602	0.06683

1977	0.3426	0.3297	0.2851	0.2241	0.1907	0.1155

1978	0.5854	0.5661	0.4963	0.4156	0.3568	0.1652

1979	0.3394	0.3292	0.2893	0.2281	0.1951	0.1045

1980	0.3352	0.3234	0.2812	0.222	0.1892	0.09895

1981	0.3244	0.3116	0.266	0.2096	0.1801	0.1039

1982	1.077	1.036	0.8919	0.6637	0.5546	0.2677

1983	0.3661	0.3539	0.3119	0.2703	0.2343	0.1284

1984	0.2991	0.288	0.246	0.1933	0.1673	0.08856

1985	0.3015	0.2896	0.249	0.1941	0.1653	0.078

1986	0.3255	0.313	0.2696	0.2089	0.1763	0.0802

1987	0.3152	0.3031	0.2647	0.2087	0.1784	0.08277

1988	0.6554	0.6359	0.5571	0.4155	0.3562	0.1418

1989	0.301	0.291	0.2513	0.1949	0.1658	0.08203

1990	0.3001	0.2889	0.2489	0.2095	0.1962	0.0882

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	1.077	1.036	0.8919	0.6637	0.5546	0.2677

0.0645161290322581	0.7069	0.6908	0.6217	0.4831	0.4179	0.2076

0.0967741935483871	0.6554	0.6359	0.5571	0.4156	0.3568	0.1652

0.129032258064516	0.6401	0.6158	0.5279	0.4155	0.3562	0.1582

0.161290322580645	0.5854	0.5661	0.4963	0.3945	0.3238	0.1458

0.193548387096774	0.5031	0.4856	0.4219	0.3171	0.2704	0.1418

0.225806451612903	0.4784	0.4602	0.3984	0.3141	0.2665	0.1284

0.258064516129032	0.4295	0.416	0.3885	0.3132	0.261	0.1166

0.290322580645161	0.3661	0.3539	0.3119	0.2703	0.2343	0.1155

0.32258064516129	0.354	0.3408	0.2942	0.2322	0.2012	0.1155

0.354838709677419	0.3493	0.3369	0.2921	0.2297	0.1967	0.1057

0.387096774193548	0.3426	0.3297	0.2893	0.2281	0.1962	0.1045

0.419354838709677	0.3394	0.3292	0.2851	0.2241	0.1951	0.1039

0.451612903225806	0.3352	0.3234	0.2812	0.222	0.1907	0.1039

0.483870967741936	0.3342	0.3209	0.2736	0.2142	0.1892	0.09895

0.516129032258065	0.3263	0.3134	0.2696	0.2101	0.184	0.0964

0.548387096774194	0.3255	0.313	0.2696	0.2096	0.1801	0.09582

0.580645161290323	0.3244	0.3116	0.266	0.2095	0.1789	0.09475

0.612903225806452	0.3227	0.3102	0.2655	0.2089	0.1784	0.09447

0.645161290322581	0.3178	0.3057	0.2647	0.2087	0.1782	0.09411

0.67741935483871	0.3152	0.3031	0.262	0.2072	0.1771	0.09315

0.709677419354839	0.3121	0.3005	0.2587	0.2046	0.1763	0.08856

0.741935483870968	0.3015	0.2924	0.2536	0.2029	0.1713	0.0882

0.774193548387097	0.301	0.291	0.2513	0.1974	0.1706	0.08277

0.806451612903226	0.3008	0.2896	0.249	0.1949	0.1673	0.08203

0.838709677419355	0.3001	0.2889	0.2489	0.1941	0.1658	0.08037

0.870967741935484	0.2995	0.288	0.2467	0.1933	0.1656	0.0802

0.903225806451613	0.2991	0.288	0.246	0.193	0.1653	0.078

0.935483870967742	0.2814	0.2713	0.2394	0.19	0.1622	0.06767

0.967741935483871	0.2703	0.2588	0.2338	0.1876	0.1602	0.06683

0.1	0.65387	0.63389	0.55418	0.41559	0.35674	0.1645

					Average of yearly averages:	0.112086

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CATURFGRD

Metfile:	w23234.dvf

PRZM scenario:	CATurfRLF.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.2912	kg/ha

Application Efficiency:	APPEFF	0.99	fraction

Spray Drift	DRFT	0.01	fraction of application rate applied to pond

Application Date	Date	1-4	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	7	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.2912	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

stored as CATF19GRD.out

Chemical: DPXE2Y45

PRZM environment: CATurfRLF.txt	modified Tueday, 20 February 2007 at
11:03:48

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
15:33:30

Metfile: w23234.dvf	modified Wedday, 3 July 2002 at 08:04:22

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.2136	0.2083	0.1838	0.1115	0.1003	0.06133

1962	1.326	1.276	1.093	0.8147	0.6703	0.2772

1963	0.5564	0.5408	0.4948	0.4247	0.3982	0.2315

1964	0.3724	0.3643	0.3172	0.2316	0.1964	0.1316

1965	0.3174	0.3102	0.1608	0.1326	0.1288	0.1038

1966	0.3015	0.2934	0.26	0.2231	0.1938	0.1403

1967	0.7896	0.765	0.7218	0.5572	0.4875	0.2536

1968	0.2864	0.2774	0.2487	0.2075	0.1891	0.1355

1969	0.2854	0.2792	0.2688	0.2442	0.2151	0.1537

1970	0.2739	0.2662	0.2475	0.1993	0.1735	0.1376

1971	0.1915	0.1856	0.1643	0.1445	0.1393	0.1019

1972	0.4698	0.4541	0.4064	0.3704	0.3154	0.1307

1973	0.4113	0.3983	0.3508	0.2644	0.2343	0.1785

1974	0.3579	0.3472	0.3128	0.2477	0.2171	0.1393

1975	0.1793	0.1735	0.1608	0.1543	0.153	0.1153

1976	0.364	0.1976	0.121	0.1184	0.1148	0.0765

1977	0.5114	0.4923	0.4232	0.3189	0.2731	0.1729

1978	0.3741	0.3648	0.3323	0.3012	0.2805	0.1719

1979	0.3512	0.3389	0.2943	0.2722	0.2493	0.1669

1980	0.371	0.3596	0.3216	0.2847	0.2606	0.1547

1981	0.4383	0.4232	0.3683	0.2899	0.2179	0.1555

1982	0.9669	0.9316	0.8036	0.6201	0.5336	0.3125

1983	0.4098	0.3978	0.3693	0.3394	0.3085	0.1943

1984	0.3107	0.3005	0.2722	0.2156	0.177	0.1336

1985	0.179	0.1729	0.1547	0.1333	0.1305	0.1097

1986	0.2724	0.2634	0.233	0.2049	0.1904	0.1218

1987	0.2068	0.1995	0.1743	0.139	0.1323	0.1053

1988	0.1591	0.1538	0.1479	0.1433	0.1433	0.09436

1989	0.1689	0.1629	0.1409	0.1221	0.117	0.09671

1990	0.1821	0.176	0.1652	0.157	0.1496	0.09281

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	1.326	1.276	1.093	0.8147	0.6703	0.3125

0.0645161290322581	0.9669	0.9316	0.8036	0.6201	0.5336	0.2772

0.0967741935483871	0.7896	0.765	0.7218	0.5572	0.4875	0.2536

0.129032258064516	0.5564	0.5408	0.4948	0.4247	0.3982	0.2315

0.161290322580645	0.5114	0.4923	0.4232	0.3704	0.3154	0.1943

0.193548387096774	0.4698	0.4541	0.4064	0.3394	0.3085	0.1785

0.225806451612903	0.4383	0.4232	0.3693	0.3189	0.2805	0.1729

0.258064516129032	0.4113	0.3983	0.3683	0.3012	0.2731	0.1719

0.290322580645161	0.4098	0.3978	0.3508	0.2899	0.2606	0.1669

0.32258064516129	0.3741	0.3648	0.3323	0.2847	0.2493	0.1555

0.354838709677419	0.3724	0.3643	0.3216	0.2722	0.2343	0.1547

0.387096774193548	0.371	0.3596	0.3172	0.2644	0.2179	0.1537

0.419354838709677	0.364	0.3472	0.3128	0.2477	0.2171	0.1403

0.451612903225806	0.3579	0.3389	0.2943	0.2442	0.2151	0.1393

0.483870967741936	0.3512	0.3102	0.2722	0.2316	0.1964	0.1376

0.516129032258065	0.3174	0.3005	0.2688	0.2231	0.1938	0.1355

0.548387096774194	0.3107	0.2934	0.26	0.2156	0.1904	0.1336

0.580645161290323	0.3015	0.2792	0.2487	0.2075	0.1891	0.1316

0.612903225806452	0.2864	0.2774	0.2475	0.2049	0.177	0.1307

0.645161290322581	0.2854	0.2662	0.233	0.1993	0.1735	0.1218

0.67741935483871	0.2739	0.2634	0.1838	0.157	0.153	0.1153

0.709677419354839	0.2724	0.2083	0.1743	0.1543	0.1496	0.1097

0.741935483870968	0.2136	0.1995	0.1652	0.1445	0.1433	0.1053

0.774193548387097	0.2068	0.1976	0.1643	0.1433	0.1393	0.1038

0.806451612903226	0.1915	0.1856	0.1608	0.139	0.1323	0.1019

0.838709677419355	0.1821	0.176	0.1608	0.1333	0.1305	0.09671

0.870967741935484	0.1793	0.1735	0.1547	0.1326	0.1288	0.09436

0.903225806451613	0.179	0.1729	0.1479	0.1221	0.117	0.09281

0.935483870967742	0.1689	0.1629	0.1409	0.1184	0.1148	0.0765

0.967741935483871	0.1591	0.1538	0.121	0.1115	0.1003	0.06133

0.1	0.76628	0.74258	0.6991	0.54395	0.47857	0.25139

					Average of yearly averages:	0.148377

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CATF19GRD

Metfile:	w23234.dvf

PRZM scenario:	CATurfRLF.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.029	kg/ha

Application Efficiency:	APPEFF	0.99	fraction

Spray Drift	DRFT	0.01	fraction of application rate applied to pond

Application Date	Date	1-4	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	7	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.029	kg/ha

Interval 2	interval	7	days	Set to 0 or delete line for single app.

app. rate 2	apprate	0.029	kg/ha

Interval 3	interval	7	days	Set to 0 or delete line for single app.

app. rate 3	apprate	0.029	kg/ha

Interval 4	interval	7	days	Set to 0 or delete line for single app.

app. rate 4	apprate	0.029	kg/ha

Interval 5	interval	7	days	Set to 0 or delete line for single app.

app. rate 5	apprate	0.029	kg/ha

Interval 6	interval	7	days	Set to 0 or delete line for single app.

app. rate 6	apprate	0.029	kg/ha

Interval 7	interval	7	days	Set to 0 or delete line for single app.

app. rate 7	apprate	0.029	kg/ha

Interval 8	interval	7	days	Set to 0 or delete line for single app.

app. rate 8	apprate	0.029	kg/ha

Interval 9	interval	7	days	Set to 0 or delete line for single app.

app. rate 9	apprate	0.029	kg/ha

Interval 10	interval	7	days	Set to 0 or delete line for single app.

app. rate 10	apprate	0.029	kg/ha

Interval 11	interval	7	days	Set to 0 or delete line for single app.

app. rate 11	apprate	0.029	kg/ha

Interval 12	interval	7	days	Set to 0 or delete line for single app.

app. rate 12	apprate	0.029	kg/ha

Interval 13	interval	7	days	Set to 0 or delete line for single app.

app. rate 13	apprate	0.029	kg/ha

Interval 14	interval	7	days	Set to 0 or delete line for single app.

app. rate 14	apprate	0.029	kg/ha

Interval 15	interval	7	days	Set to 0 or delete line for single app.

app. rate 15	apprate	0.029	kg/ha

Interval 16	interval	7	days	Set to 0 or delete line for single app.

app. rate 16	apprate	0.029	kg/ha

Interval 17	interval	7	days	Set to 0 or delete line for single app.

app. rate 17	apprate	0.029	kg/ha

Interval 18	interval	7	days	Set to 0 or delete line for single app.

app. rate 18	apprate	0.029	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

FL Nursey

stored as FLnursey.out

Chemical: DPXE2Y45

PRZM environment: FLnurserySTD.txt	modified Wedday, 24 January 2007 at
09:18:06

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w12839.dvf	modified Wedday, 3 July 2002 at 09:04:28

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	2.519	2.429	2.224	1.837	1.532	0.6908

1962	1.426	1.38	1.258	0.9451	0.7806	0.4549

1963	2.805	2.69	2.281	1.823	1.522	0.8256

1964	1.755	1.686	1.458	1.264	1.113	0.4965

1965	3.097	2.964	2.489	2.01	1.739	0.7263

1966	11.38	10.91	9.375	7.136	5.955	2.191

1967	2.415	2.328	2.044	1.523	1.314	0.7161

1968	2.888	2.808	2.616	2.088	1.743	0.7756

1969	3.539	3.391	2.866	2.235	2.081	0.9048

1970	3.17	3.073	2.668	2.022	1.67	0.8217

1971	2.775	2.666	2.393	2.103	1.842	0.702

1972	1.583	1.518	1.294	1.129	1.045	0.5567

1973	1.096	1.053	0.9011	0.7454	0.6782	0.3778

1974	2.675	2.599	2.257	1.754	1.731	0.8377

1975	0.7701	0.7393	0.6349	0.5708	0.5098	0.254

1976	2.605	2.496	2.099	1.743	1.737	0.8241

1977	9.968	9.565	8.27	6.273	5.151	2.031

1978	2.487	2.394	2.182	1.838	1.63	0.69

1979	26.6	25.43	21.55	15.56	12.58	4.136

1980	8.136	7.866	6.933	5.458	5.12	2.045

1981	5.438	5.211	4.389	3.147	2.679	1.071

1982	5.104	4.993	4.32	3.167	2.58	1.008

1983	6.137	5.897	5.139	4.349	3.672	1.336

1984	7.769	7.42	6.19	5.568	4.844	1.774

1985	1.177	1.129	0.9598	0.8162	0.7716	0.3966

1986	4.494	4.309	3.763	3.047	2.592	0.973

1987	2.691	2.584	2.196	1.969	1.691	0.6992

1988	2.201	2.12	1.927	1.58	1.329	0.5402

1989	1.259	1.221	1.083	0.8204	0.7084	0.3

1990	4.786	4.581	3.9	2.937	2.461	0.8867

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	26.6	25.43	21.55	15.56	12.58	4.136

0.0645161290322581	11.38	10.91	9.375	7.136	5.955	2.191

0.0967741935483871	9.968	9.565	8.27	6.273	5.151	2.045

0.129032258064516	8.136	7.866	6.933	5.568	5.12	2.031

0.161290322580645	7.769	7.42	6.19	5.458	4.844	1.774

0.193548387096774	6.137	5.897	5.139	4.349	3.672	1.336

0.225806451612903	5.438	5.211	4.389	3.167	2.679	1.071

0.258064516129032	5.104	4.993	4.32	3.147	2.592	1.008

0.290322580645161	4.786	4.581	3.9	3.047	2.58	0.973

0.32258064516129	4.494	4.309	3.763	2.937	2.461	0.9048

0.354838709677419	3.539	3.391	2.866	2.235	2.081	0.8867

0.387096774193548	3.17	3.073	2.668	2.103	1.842	0.8377

0.419354838709677	3.097	2.964	2.616	2.088	1.743	0.8256

0.451612903225806	2.888	2.808	2.489	2.022	1.739	0.8241

0.483870967741936	2.805	2.69	2.393	2.01	1.737	0.8217

0.516129032258065	2.775	2.666	2.281	1.969	1.731	0.7756

0.548387096774194	2.691	2.599	2.257	1.838	1.691	0.7263

0.580645161290323	2.675	2.584	2.224	1.837	1.67	0.7161

0.612903225806452	2.605	2.496	2.196	1.823	1.63	0.702

0.645161290322581	2.519	2.429	2.182	1.754	1.532	0.6992

0.67741935483871	2.487	2.394	2.099	1.743	1.522	0.6908

0.709677419354839	2.415	2.328	2.044	1.58	1.329	0.69

0.741935483870968	2.201	2.12	1.927	1.523	1.314	0.5567

0.774193548387097	1.755	1.686	1.458	1.264	1.113	0.5402

0.806451612903226	1.583	1.518	1.294	1.129	1.045	0.4965

0.838709677419355	1.426	1.38	1.258	0.9451	0.7806	0.4549

0.870967741935484	1.259	1.221	1.083	0.8204	0.7716	0.3966

0.903225806451613	1.177	1.129	0.9598	0.8162	0.7084	0.3778

0.935483870967742	1.096	1.053	0.9011	0.7454	0.6782	0.3

0.967741935483871	0.7701	0.7393	0.6349	0.5708	0.5098	0.254

0.1	9.7848	9.3951	8.1363	6.2025	5.1479	2.0436

					Average of yearly averages:	1.00141

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: FLnursey

Metfile:	w12839.dvf

PRZM scenario:	FLnurserySTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.5591	kg/ha

Application Efficiency:	APPEFF	0.99	fraction

Spray Drift	DRFT	0.01	fraction of application rate applied to pond

Application Date	Date	1-2	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval		days	Set to 0 or delete line for single app.

app. rate 1	apprate		kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

FL Cabbage

stored as FLCABAIR.out

Chemical: DPXE2Y45

PRZM environment: FLcabbageSTD.txt	modified Thuday, 24 May 2007 at
09:40:46

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w12842.dvf	modified Wedday, 3 July 2002 at 09:04:28

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	1.57	1.504	0.9523	0.5357	0.4295	0.1059

1962	1.237	1.19	1.024	0.7657	0.6498	0.3023

1963	4.429	4.292	3.634	2.51	1.749	0.4925

1964	1.796	1.747	1.626	1.329	1.141	0.5567

1965	0.952	0.917	0.799	0.6196	0.5475	0.2825

1966	0.6769	0.6544	0.5866	0.4964	0.4386	0.2236

1967	0.5583	0.5369	0.4595	0.3566	0.3104	0.165

1968	1.967	1.886	1.637	1.382	1.073	0.3693

1969	1.179	1.143	0.9789	0.7889	0.6218	0.366

1970	0.7665	0.7517	0.6723	0.5257	0.4473	0.2274

1971	1.018	0.9754	0.8503	0.6403	0.494	0.2548

1972	1.114	1.066	0.933	0.8296	0.6451	0.3019

1973	1.319	1.259	1.061	0.8634	0.6583	0.2942

1974	0.9926	0.9586	0.7198	0.4394	0.3725	0.2192

1975	1.595	1.524	1.274	0.9137	0.6984	0.3149

1976	0.6341	0.6193	0.5358	0.4467	0.3525	0.2272

1977	0.7478	0.7187	0.663	0.5103	0.4182	0.1963

1978	1.457	1.397	1.188	0.8622	0.6682	0.2707

1979	0.7743	0.7489	0.7076	0.5756	0.4955	0.2446

1980	0.9727	0.9362	0.8462	0.6225	0.493	0.2119

1981	1.41	1.36	0.6545	0.4951	0.4502	0.2581

1982	1.271	1.218	1.069	0.8186	0.6956	0.3322

1983	1.002	0.9802	0.857	0.589	0.4734	0.2531

1984	0.7922	0.7665	0.673	0.5206	0.4387	0.2126

1985	4.224	4.086	3.438	2.456	1.737	0.5007

1986	2.343	2.265	1.916	1.452	1.089	0.5599

1987	1.829	1.754	1.52	1.169	0.8622	0.4056

1988	2.686	2.57	2.172	1.467	1.059	0.4289

1989	1.352	1.294	1.13	0.9166	0.7426	0.4266

1990	0.689	0.6655	0.5797	0.4508	0.3828	0.1949

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	4.429	4.292	3.634	2.51	1.749	0.5599

0.0645161290322581	4.224	4.086	3.438	2.456	1.737	0.5567

0.0967741935483871	2.686	2.57	2.172	1.467	1.141	0.5007

0.129032258064516	2.343	2.265	1.916	1.452	1.089	0.4925

0.161290322580645	1.967	1.886	1.637	1.382	1.073	0.4289

0.193548387096774	1.829	1.754	1.626	1.329	1.059	0.4266

0.225806451612903	1.796	1.747	1.52	1.169	0.8622	0.4056

0.258064516129032	1.595	1.524	1.274	0.9166	0.7426	0.3693

0.290322580645161	1.57	1.504	1.188	0.9137	0.6984	0.366

0.32258064516129	1.457	1.397	1.13	0.8634	0.6956	0.3322

0.354838709677419	1.41	1.36	1.069	0.8622	0.6682	0.3149

0.387096774193548	1.352	1.294	1.061	0.8296	0.6583	0.3023

0.419354838709677	1.319	1.259	1.024	0.8186	0.6498	0.3019

0.451612903225806	1.271	1.218	0.9789	0.7889	0.6451	0.2942

0.483870967741936	1.237	1.19	0.9523	0.7657	0.6218	0.2825

0.516129032258065	1.179	1.143	0.933	0.6403	0.5475	0.2707

0.548387096774194	1.114	1.066	0.857	0.6225	0.4955	0.2581

0.580645161290323	1.018	0.9802	0.8503	0.6196	0.494	0.2548

0.612903225806452	1.002	0.9754	0.8462	0.589	0.493	0.2531

0.645161290322581	0.9926	0.9586	0.799	0.5756	0.4734	0.2446

0.67741935483871	0.9727	0.9362	0.7198	0.5357	0.4502	0.2274

0.709677419354839	0.952	0.917	0.7076	0.5257	0.4473	0.2272

0.741935483870968	0.7922	0.7665	0.673	0.5206	0.4387	0.2236

0.774193548387097	0.7743	0.7517	0.6723	0.5103	0.4386	0.2192

0.806451612903226	0.7665	0.7489	0.663	0.4964	0.4295	0.2126

0.838709677419355	0.7478	0.7187	0.6545	0.4951	0.4182	0.2119

0.870967741935484	0.689	0.6655	0.5866	0.4508	0.3828	0.1963

0.903225806451613	0.6769	0.6544	0.5797	0.4467	0.3725	0.1949

0.935483870967742	0.6341	0.6193	0.5358	0.4394	0.3525	0.165

0.967741935483871	0.5583	0.5369	0.4595	0.3566	0.3104	0.1059

0.1	2.6517	2.5395	2.1464	1.4655	1.1358	0.49988

					Average of yearly averages:	0.30665

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: FLCABAIR

Metfile:	w12842.dvf

PRZM scenario:	FLcabbageSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.0728	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.05	fraction of application rate applied to pond

Application Date	Date	16-10	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	3	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.0728	kg/ha

Interval 2	interval	3	days	Set to 0 or delete line for single app.

app. rate 2	apprate	0.0728	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

stored as FLCABGRD.out

Chemical: DPXE2Y45

PRZM environment: FLcabbageSTD.txt	modified Thuday, 24 May 2007 at
09:40:46

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w12842.dvf	modified Wedday, 3 July 2002 at 09:04:28

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	1.498	1.434	0.859	0.3601	0.2545	0.06276

1962	1.177	1.132	0.9691	0.7203	0.6103	0.2414

1963	4.329	4.197	3.55	2.412	1.624	0.4375

1964	1.748	1.7	1.585	1.295	1.112	0.5009

1965	0.8685	0.8358	0.7266	0.5615	0.4977	0.2177

1966	0.6139	0.5925	0.5299	0.4327	0.3839	0.1566

1967	0.4246	0.4073	0.3451	0.2234	0.1835	0.09855

1968	1.766	1.692	1.464	1.183	0.9204	0.3109

1969	1.055	1.02	0.8715	0.6098	0.4922	0.3041

1970	0.6782	0.6658	0.5945	0.4619	0.3915	0.16

1971	0.6281	0.6108	0.5491	0.4084	0.3165	0.1923

1972	0.782	0.7477	0.6785	0.6343	0.469	0.2394

1973	1.028	0.981	0.8289	0.7007	0.4932	0.2308

1974	0.8899	0.8567	0.6145	0.3556	0.2999	0.1566

1975	1.284	1.227	1.024	0.726	0.5342	0.256

1976	0.358	0.3468	0.3055	0.2383	0.2301	0.1631

1977	0.5492	0.5269	0.4975	0.3226	0.2334	0.1262

1978	1.143	1.095	0.9278	0.675	0.4976	0.2045

1979	0.6928	0.6698	0.6343	0.5171	0.4454	0.1807

1980	0.755	0.7258	0.6646	0.439	0.3114	0.1454

1981	1.351	1.3	0.6188	0.4642	0.3986	0.1957

1982	1.214	1.162	1.02	0.7783	0.6608	0.2736

1983	0.8856	0.863	0.7501	0.4091	0.3007	0.1886

1984	0.7023	0.6787	0.5931	0.4552	0.3823	0.147

1985	4.05	3.921	3.297	2.353	1.616	0.4507

1986	2.054	1.981	1.678	1.284	0.9378	0.5109

1987	1.576	1.511	1.313	1.016	0.7014	0.3481

1988	2.584	2.471	2.086	1.335	0.9129	0.3747

1989	1.232	1.185	1.019	0.7868	0.6618	0.3749

1990	0.6054	0.5843	0.5073	0.3938	0.3344	0.1328

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	4.329	4.197	3.55	2.412	1.624	0.5109

0.0645161290322581	4.05	3.921	3.297	2.353	1.616	0.5009

0.0967741935483871	2.584	2.471	2.086	1.335	1.112	0.4507

0.129032258064516	2.054	1.981	1.678	1.295	0.9378	0.4375

0.161290322580645	1.766	1.7	1.585	1.284	0.9204	0.3749

0.193548387096774	1.748	1.692	1.464	1.183	0.9129	0.3747

0.225806451612903	1.576	1.511	1.313	1.016	0.7014	0.3481

0.258064516129032	1.498	1.434	1.024	0.7868	0.6618	0.3109

0.290322580645161	1.351	1.3	1.02	0.7783	0.6608	0.3041

0.32258064516129	1.284	1.227	1.019	0.726	0.6103	0.2736

0.354838709677419	1.232	1.185	0.9691	0.7203	0.5342	0.256

0.387096774193548	1.214	1.162	0.9278	0.7007	0.4977	0.2414

0.419354838709677	1.177	1.132	0.8715	0.675	0.4976	0.2394

0.451612903225806	1.143	1.095	0.859	0.6343	0.4932	0.2308

0.483870967741936	1.055	1.02	0.8289	0.6098	0.4922	0.2177

0.516129032258065	1.028	0.981	0.7501	0.5615	0.469	0.2045

0.548387096774194	0.8899	0.863	0.7266	0.5171	0.4454	0.1957

0.580645161290323	0.8856	0.8567	0.6785	0.4642	0.3986	0.1923

0.612903225806452	0.8685	0.8358	0.6646	0.4619	0.3915	0.1886

0.645161290322581	0.782	0.7477	0.6343	0.4552	0.3839	0.1807

0.67741935483871	0.755	0.7258	0.6188	0.439	0.3823	0.1631

0.709677419354839	0.7023	0.6787	0.6145	0.4327	0.3344	0.16

0.741935483870968	0.6928	0.6698	0.5945	0.4091	0.3165	0.1566

0.774193548387097	0.6782	0.6658	0.5931	0.4084	0.3114	0.1566

0.806451612903226	0.6281	0.6108	0.5491	0.3938	0.3007	0.147

0.838709677419355	0.6139	0.5925	0.5299	0.3601	0.2999	0.1454

0.870967741935484	0.6054	0.5843	0.5073	0.3556	0.2545	0.1328

0.903225806451613	0.5492	0.5269	0.4975	0.3226	0.2334	0.1262

0.935483870967742	0.4246	0.4073	0.3451	0.2383	0.2301	0.09855

0.967741935483871	0.358	0.3468	0.3055	0.2234	0.1835	0.06276

0.1	2.531	2.422	2.0452	1.331	1.09458	0.44938

					Average of yearly averages:	0.246080333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: FLCABGRD

Metfile:	w12842.dvf

PRZM scenario:	FLcabbageSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.0728	kg/ha

Application Efficiency:	APPEFF	0.99	fraction

Spray Drift	DRFT	0.01	fraction of application rate applied to pond

Application Date	Date	16-10	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	3	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.0728	kg/ha

Interval 2	interval	3	days	Set to 0 or delete line for single app.

app. rate 2	apprate	0.0728	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

FL Cucumber

stored as FLCUCAIR.out

Chemical: DPXE2Y45

PRZM environment: FLcucumberSTD.txt	modified Wedday, 13 June 2007 at
11:19:24

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w12844.dvf	modified Wedday, 3 July 2002 at 09:04:30

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	1.957	1.876	1.591	1.186	0.9082	0.2239

1962	1.165	1.116	0.9448	0.695	0.5566	0.2812

1963	1.693	1.629	1.425	1.251	1.048	0.3982

1964	3.226	3.098	2.647	2.379	1.741	0.7633

1965	7.096	6.872	5.832	4.3	3.212	1.102

1966	3.957	3.815	3.265	2.396	1.802	1.008

1967	2.335	2.242	1.9	1.406	1.056	0.5401

1968	1.96	1.882	1.642	1.337	1.034	0.4253

1969	4.387	4.258	3.681	2.765	2.102	0.7688

1970	1.36	1.323	1.19	0.9648	0.8372	0.3925

1971	3.1	2.98	2.595	1.954	1.486	0.4604

1972	8.095	7.776	6.626	4.65	3.187	1.017

1973	3.059	2.967	2.66	2.121	1.811	0.7887

1974	1.607	1.543	1.327	1.006	0.8165	0.4213

1975	1.039	0.9971	0.9272	0.7697	0.5958	0.3096

1976	2.845	2.738	2.349	1.797	1.312	0.4253

1977	2.245	2.18	1.892	1.266	0.9322	0.5128

1978	3.82	3.731	3.265	2.548	1.899	0.7031

1979	1.486	1.442	1.276	0.9987	0.8462	0.5064

1980	0.8746	0.8516	0.7737	0.6597	0.53	0.2741

1981	4.912	4.691	3.91	2.737	1.902	0.5653

1982	5.694	5.501	4.952	3.771	2.652	1.117

1983	3.939	3.785	3.502	2.685	2.011	0.9462

1984	4.937	4.747	4.068	2.997	2.143	0.8185

1985	2.257	2.174	1.876	1.417	1.193	0.5269

1986	3.206	3.095	2.885	2.32	1.772	0.741

1987	5.685	5.493	4.826	3.541	2.447	0.8523

1988	2.038	1.989	1.783	1.415	1.205	0.6471

1989	1.419	1.362	1.151	0.8318	0.674	0.3106

1990	1.511	1.445	1.21	0.8619	0.6534	0.323

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	8.095	7.776	6.626	4.65	3.212	1.117

0.0645161290322581	7.096	6.872	5.832	4.3	3.187	1.102

0.0967741935483871	5.694	5.501	4.952	3.771	2.652	1.017

0.129032258064516	5.685	5.493	4.826	3.541	2.447	1.008

0.161290322580645	4.937	4.747	4.068	2.997	2.143	0.9462

0.193548387096774	4.912	4.691	3.91	2.765	2.102	0.8523

0.225806451612903	4.387	4.258	3.681	2.737	2.011	0.8185

0.258064516129032	3.957	3.815	3.502	2.685	1.902	0.7887

0.290322580645161	3.939	3.785	3.265	2.548	1.899	0.7688

0.32258064516129	3.82	3.731	3.265	2.396	1.811	0.7633

0.354838709677419	3.226	3.098	2.885	2.379	1.802	0.741

0.387096774193548	3.206	3.095	2.66	2.32	1.772	0.7031

0.419354838709677	3.1	2.98	2.647	2.121	1.741	0.6471

0.451612903225806	3.059	2.967	2.595	1.954	1.486	0.5653

0.483870967741936	2.845	2.738	2.349	1.797	1.312	0.5401

0.516129032258065	2.335	2.242	1.9	1.417	1.205	0.5269

0.548387096774194	2.257	2.18	1.892	1.415	1.193	0.5128

0.580645161290323	2.245	2.174	1.876	1.406	1.056	0.5064

0.612903225806452	2.038	1.989	1.783	1.337	1.048	0.4604

0.645161290322581	1.96	1.882	1.642	1.266	1.034	0.4253

0.67741935483871	1.957	1.876	1.591	1.251	0.9322	0.4253

0.709677419354839	1.693	1.629	1.425	1.186	0.9082	0.4213

0.741935483870968	1.607	1.543	1.327	1.006	0.8462	0.3982

0.774193548387097	1.511	1.445	1.276	0.9987	0.8372	0.3925

0.806451612903226	1.486	1.442	1.21	0.9648	0.8165	0.323

0.838709677419355	1.419	1.362	1.19	0.8619	0.674	0.3106

0.870967741935484	1.36	1.323	1.151	0.8318	0.6534	0.3096

0.903225806451613	1.165	1.116	0.9448	0.7697	0.5958	0.2812

0.935483870967742	1.039	0.9971	0.9272	0.695	0.5566	0.2741

0.967741935483871	0.8746	0.8516	0.7737	0.6597	0.53	0.2239

0.1	5.6931	5.5002	4.9394	3.748	2.6315	1.0161

					Average of yearly averages:	0.605663333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: FLCUCAIR

Metfile:	w12844.dvf

PRZM scenario:	FLcucumberSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.0728	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.05	fraction of application rate applied to pond

Application Date	Date	16-10	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	3	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.0728	kg/ha

Interval 2	interval	3	days	Set to 0 or delete line for single app.

app. rate 2	apprate	0.0728	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

stored as FLCUCGRD.out

Chemical: DPXE2Y45

PRZM environment: FLcucumberSTD.txt	modified Wedday, 13 June 2007 at
11:19:24

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w12844.dvf	modified Wedday, 3 July 2002 at 09:04:30

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	1.669	1.599	1.357	0.9868	0.75	0.1849

1962	0.7889	0.7554	0.6399	0.4701	0.377	0.2176

1963	1.554	1.421	1.22	1.056	0.8879	0.337

1964	2.996	2.876	2.452	2.246	1.607	0.7155

1965	7.044	6.817	5.789	4.232	3.15	1.072

1966	3.686	3.556	3.047	2.238	1.676	0.9728

1967	2.014	1.933	1.638	1.216	0.8961	0.4857

1968	1.614	1.55	1.358	1.129	0.8736	0.3655

1969	4.183	4.063	3.518	2.628	1.987	0.7223

1970	1.301	1.266	1.139	0.9231	0.8008	0.333

1971	2.901	2.787	2.421	1.801	1.343	0.405

1972	8.124	7.803	6.646	4.635	3.117	0.9831

1973	3.064	2.971	2.664	2.123	1.813	0.7447

1974	1.423	1.365	1.173	0.8411	0.6494	0.3648

1975	0.7975	0.765	0.6635	0.5467	0.4224	0.248

1976	2.628	2.528	2.167	1.657	1.161	0.3674

1977	2.114	2.055	1.784	1.115	0.7733	0.457

1978	3.679	3.586	3.146	2.411	1.778	0.6572

1979	1.43	1.387	1.226	0.9578	0.8118	0.4523

1980	0.6931	0.6763	0.5828	0.4659	0.3494	0.21

1981	4.8	4.584	3.817	2.654	1.788	0.5157

1982	5.627	5.438	4.872	3.719	2.562	1.09

1983	3.679	3.536	3.305	2.55	1.895	0.9107

1984	4.922	4.728	4.051	2.923	2.038	0.7791

1985	2.24	2.158	1.86	1.403	1.18	0.4781

1986	2.938	2.891	2.66	2.162	1.651	0.7001

1987	5.599	5.399	4.751	3.481	2.348	0.8137

1988	2.004	1.955	1.753	1.39	1.183	0.5997

1989	1.065	1.023	0.8664	0.6273	0.5054	0.2526

1990	1.141	1.091	0.9133	0.6506	0.4854	0.264

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	8.124	7.803	6.646	4.635	3.15	1.09

0.0645161290322581	7.044	6.817	5.789	4.232	3.117	1.072

0.0967741935483871	5.627	5.438	4.872	3.719	2.562	0.9831

0.129032258064516	5.599	5.399	4.751	3.481	2.348	0.9728

0.161290322580645	4.922	4.728	4.051	2.923	2.038	0.9107

0.193548387096774	4.8	4.584	3.817	2.654	1.987	0.8137

0.225806451612903	4.183	4.063	3.518	2.628	1.895	0.7791

0.258064516129032	3.686	3.586	3.305	2.55	1.813	0.7447

0.290322580645161	3.679	3.556	3.146	2.411	1.788	0.7223

0.32258064516129	3.679	3.536	3.047	2.246	1.778	0.7155

0.354838709677419	3.064	2.971	2.664	2.238	1.676	0.7001

0.387096774193548	2.996	2.891	2.66	2.162	1.651	0.6572

0.419354838709677	2.938	2.876	2.452	2.123	1.607	0.5997

0.451612903225806	2.901	2.787	2.421	1.801	1.343	0.5157

0.483870967741936	2.628	2.528	2.167	1.657	1.183	0.4857

0.516129032258065	2.24	2.158	1.86	1.403	1.18	0.4781

0.548387096774194	2.114	2.055	1.784	1.39	1.161	0.457

0.580645161290323	2.014	1.955	1.753	1.216	0.8961	0.4523

0.612903225806452	2.004	1.933	1.638	1.129	0.8879	0.405

0.645161290322581	1.669	1.599	1.358	1.115	0.8736	0.3674

0.67741935483871	1.614	1.55	1.357	1.056	0.8118	0.3655

0.709677419354839	1.554	1.421	1.226	0.9868	0.8008	0.3648

0.741935483870968	1.43	1.387	1.22	0.9578	0.7733	0.337

0.774193548387097	1.423	1.365	1.173	0.9231	0.75	0.333

0.806451612903226	1.301	1.266	1.139	0.8411	0.6494	0.264

0.838709677419355	1.141	1.091	0.9133	0.6506	0.5054	0.2526

0.870967741935484	1.065	1.023	0.8664	0.6273	0.4854	0.248

0.903225806451613	0.7975	0.765	0.6635	0.5467	0.4224	0.2176

0.935483870967742	0.7889	0.7554	0.6399	0.4701	0.377	0.21

0.967741935483871	0.6931	0.6763	0.5828	0.4659	0.3494	0.1849

0.1	5.6242	5.4341	4.8599	3.6952	2.5406	0.98207

					Average of yearly averages:	0.55665

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: FLCUCGRD

Metfile:	w12844.dvf

PRZM scenario:	FLcucumberSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.0728	kg/ha

Application Efficiency:	APPEFF	0.99	fraction

Spray Drift	DRFT	0.01	fraction of application rate applied to pond

Application Date	Date	16-10	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	3	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.0728	kg/ha

Interval 2	interval	3	days	Set to 0 or delete line for single app.

app. rate 2	apprate	0.0728	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

FL Pepper

stored as FLPEPAIR.out

Chemical: DPXE2Y45

PRZM environment: FLpeppersSTD.txt	modified Thuday, 24 May 2007 at
09:44:22

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w12844.dvf	modified Wedday, 3 July 2002 at 09:04:30

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	1.316	1.26	1.093	0.9206	0.7992	0.2289

1962	4.773	4.594	4.026	2.921	2.398	0.7324

1963	3.28	3.212	2.969	2.431	2.029	0.7821

1964	5.151	5.019	4.583	3.591	2.98	1.01

1965	4.786	4.586	3.983	2.925	2.372	0.9019

1966	3.556	3.458	3.324	2.707	2.291	0.9386

1967	4.095	3.949	3.624	3.075	2.567	0.8872

1968	3.835	3.756	3.374	2.55	2.175	0.855

1969	3.961	3.81	3.619	2.826	2.359	0.8713

1970	3.606	3.458	3.243	2.555	2.1	0.7771

1971	2.835	2.723	2.379	1.942	1.668	0.6312

1972	3.69	3.551	3.046	2.201	1.776	0.6878

1973	2.699	2.629	2.325	1.805	1.509	0.738

1974	2.806	2.694	2.315	1.86	1.655	0.5912

1975	6.81	6.519	5.704	4.208	3.454	1.091

1976	5.799	5.561	4.792	3.595	2.992	1.105

1977	6.199	5.965	5.491	4.449	3.698	1.304

1978	2.007	1.932	1.677	1.377	1.23	0.641

1979	8.948	8.59	7.512	5.532	4.545	1.383

1980	2.795	2.676	2.263	1.829	1.579	0.798

1981	4.804	4.634	3.957	3.112	2.617	0.8516

1982	2.733	2.625	2.336	1.894	1.603	0.6676

1983	4.467	4.276	3.627	2.656	2.173	0.7597

1984	3.618	3.471	3.082	2.348	1.964	0.7407

1985	5.276	5.05	4.468	3.34	2.717	0.9128

1986	1.766	1.718	1.479	1.214	1.149	0.5519

1987	4.138	3.966	3.509	2.855	2.379	0.78

1988	2.402	2.294	1.912	1.523	1.264	0.5688

1989	2.09	1.997	1.76	1.497	1.264	0.4898

1990	7.377	7.052	6.316	4.64	3.767	1.138

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	8.948	8.59	7.512	5.532	4.545	1.383

0.0645161290322581	7.377	7.052	6.316	4.64	3.767	1.304

0.0967741935483871	6.81	6.519	5.704	4.449	3.698	1.138

0.129032258064516	6.199	5.965	5.491	4.208	3.454	1.105

0.161290322580645	5.799	5.561	4.792	3.595	2.992	1.091

0.193548387096774	5.276	5.05	4.583	3.591	2.98	1.01

0.225806451612903	5.151	5.019	4.468	3.34	2.717	0.9386

0.258064516129032	4.804	4.634	4.026	3.112	2.617	0.9128

0.290322580645161	4.786	4.594	3.983	3.075	2.567	0.9019

0.32258064516129	4.773	4.586	3.957	2.925	2.398	0.8872

0.354838709677419	4.467	4.276	3.627	2.921	2.379	0.8713

0.387096774193548	4.138	3.966	3.624	2.855	2.372	0.855

0.419354838709677	4.095	3.949	3.619	2.826	2.359	0.8516

0.451612903225806	3.961	3.81	3.509	2.707	2.291	0.798

0.483870967741936	3.835	3.756	3.374	2.656	2.175	0.7821

0.516129032258065	3.69	3.551	3.324	2.555	2.173	0.78

0.548387096774194	3.618	3.471	3.243	2.55	2.1	0.7771

0.580645161290323	3.606	3.458	3.082	2.431	2.029	0.7597

0.612903225806452	3.556	3.458	3.046	2.348	1.964	0.7407

0.645161290322581	3.28	3.212	2.969	2.201	1.776	0.738

0.67741935483871	2.835	2.723	2.379	1.942	1.668	0.7324

0.709677419354839	2.806	2.694	2.336	1.894	1.655	0.6878

0.741935483870968	2.795	2.676	2.325	1.86	1.603	0.6676

0.774193548387097	2.733	2.629	2.315	1.829	1.579	0.641

0.806451612903226	2.699	2.625	2.263	1.805	1.509	0.6312

0.838709677419355	2.402	2.294	1.912	1.523	1.264	0.5912

0.870967741935484	2.09	1.997	1.76	1.497	1.264	0.5688

0.903225806451613	2.007	1.932	1.677	1.377	1.23	0.5519

0.935483870967742	1.766	1.718	1.479	1.214	1.149	0.4898

0.967741935483871	1.316	1.26	1.093	0.9206	0.7992	0.2289

0.1	6.7489	6.4636	5.6827	4.4249	3.6736	1.1347

					Average of yearly averages:	0.813853333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: FLPEPAIR

Metfile:	w12844.dvf

PRZM scenario:	FLpeppersSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1098	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.05	fraction of application rate applied to pond

Application Date	Date	1-9	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	5	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1098	kg/ha

Interval 2	interval	5	days	Set to 0 or delete line for single app.

app. rate 2	apprate	0.1098	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

stored as FLPEPGRD.out

Chemical: DPXE2Y45

PRZM environment: FLpeppersSTD.txt	modified Thuday, 24 May 2007 at
09:44:22

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w12844.dvf	modified Wedday, 3 July 2002 at 09:04:30

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.8142	0.7789	0.6798	0.6246	0.5451	0.1511

1962	4.479	4.298	3.774	2.734	2.24	0.65

1963	2.903	2.831	2.638	2.15	1.8	0.6962

1964	4.869	4.732	4.297	3.388	2.813	0.9318

1965	4.659	4.462	3.872	2.841	2.264	0.8237

1966	3.15	3.046	2.947	2.425	2.056	0.8599

1967	3.865	3.727	3.354	2.861	2.393	0.8057

1968	3.569	3.497	3.129	2.357	1.959	0.7732

1969	3.626	3.49	3.29	2.577	2.135	0.7869

1970	3.289	3.153	2.9	2.314	1.905	0.6946

1971	2.333	2.241	1.97	1.639	1.419	0.5424

1972	3.634	3.495	2.992	2.14	1.648	0.6029

1973	2.262	2.182	1.949	1.528	1.263	0.6549

1974	2.547	2.445	2.1	1.629	1.409	0.5045

1975	6.555	6.274	5.504	4.041	3.319	1.025

1976	5.437	5.213	4.49	3.383	2.818	1.038

1977	6.014	5.789	5.215	4.255	3.538	1.246

1978	1.693	1.628	1.408	1.098	0.9637	0.555

1979	8.728	8.378	7.329	5.39	4.424	1.326

1980	2.35	2.25	1.893	1.527	1.331	0.72

1981	4.496	4.328	3.699	2.87	2.425	0.777

1982	2.456	2.358	2.058	1.689	1.433	0.5844

1983	4.179	3.999	3.39	2.476	2.021	0.6794

1984	3.32	3.185	2.781	2.139	1.795	0.6617

1985	4.969	4.756	4.218	3.154	2.567	0.8435

1986	1.563	1.523	1.311	0.9701	0.8959	0.4688

1987	3.866	3.704	3.261	2.632	2.197	0.7028

1988	2.148	2.05	1.703	1.375	1.132	0.4855

1989	1.645	1.571	1.406	1.252	1.053	0.4054

1990	7.161	6.845	6.157	4.529	3.676	1.078

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	8.728	8.378	7.329	5.39	4.424	1.326

0.0645161290322581	7.161	6.845	6.157	4.529	3.676	1.246

0.0967741935483871	6.555	6.274	5.504	4.255	3.538	1.078

0.129032258064516	6.014	5.789	5.215	4.041	3.319	1.038

0.161290322580645	5.437	5.213	4.49	3.388	2.818	1.025

0.193548387096774	4.969	4.756	4.297	3.383	2.813	0.9318

0.225806451612903	4.869	4.732	4.218	3.154	2.567	0.8599

0.258064516129032	4.659	4.462	3.872	2.87	2.425	0.8435

0.290322580645161	4.496	4.328	3.774	2.861	2.393	0.8237

0.32258064516129	4.479	4.298	3.699	2.841	2.264	0.8057

0.354838709677419	4.179	3.999	3.39	2.734	2.24	0.7869

0.387096774193548	3.866	3.727	3.354	2.632	2.197	0.777

0.419354838709677	3.865	3.704	3.29	2.577	2.135	0.7732

0.451612903225806	3.634	3.497	3.261	2.476	2.056	0.72

0.483870967741936	3.626	3.495	3.129	2.425	2.021	0.7028

0.516129032258065	3.569	3.49	2.992	2.357	1.959	0.6962

0.548387096774194	3.32	3.185	2.947	2.314	1.905	0.6946

0.580645161290323	3.289	3.153	2.9	2.15	1.8	0.6794

0.612903225806452	3.15	3.046	2.781	2.14	1.795	0.6617

0.645161290322581	2.903	2.831	2.638	2.139	1.648	0.6549

0.67741935483871	2.547	2.445	2.1	1.689	1.433	0.65

0.709677419354839	2.456	2.358	2.058	1.639	1.419	0.6029

0.741935483870968	2.35	2.25	1.97	1.629	1.409	0.5844

0.774193548387097	2.333	2.241	1.949	1.528	1.331	0.555

0.806451612903226	2.262	2.182	1.893	1.527	1.263	0.5424

0.838709677419355	2.148	2.05	1.703	1.375	1.132	0.5045

0.870967741935484	1.693	1.628	1.408	1.252	1.053	0.4855

0.903225806451613	1.645	1.571	1.406	1.098	0.9637	0.4688

0.935483870967742	1.563	1.523	1.311	0.9701	0.8959	0.4054

0.967741935483871	0.8142	0.7789	0.6798	0.6246	0.5451	0.1511

0.1	6.5009	6.2255	5.4751	4.2336	3.5161	1.074

					Average of yearly averages:	0.73581

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: FLPEPGRD

Metfile:	w12844.dvf

PRZM scenario:	FLpeppersSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1098	kg/ha

Application Efficiency:	APPEFF	0.99	fraction

Spray Drift	DRFT	0.01	fraction of application rate applied to pond

Application Date	Date	1-9	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	5	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1098	kg/ha

Interval 2	interval	5	days	Set to 0 or delete line for single app.

app. rate 2	apprate	0.1098	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

FL Tomato

stored as FLTOMAIR.out

Chemical: DPXE2Y45

PRZM environment: FLtomatoSTD.txt	modified Tueday, 29 May 2007 at
12:54:10

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w12844.dvf	modified Wedday, 3 July 2002 at 09:04:30

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	1.534	1.472	1.389	1.076	0.8949	0.3531

1962	1.586	1.523	1.327	1.022	0.8514	0.3713

1963	0.8275	0.7959	0.6812	0.5225	0.4605	0.2431

1964	1.929	1.85	1.612	1.198	1.035	0.4031

1965	1.217	1.177	1.005	0.785	0.6706	0.2794

1966	4.861	4.671	3.995	2.995	2.46	0.8862

1967	1.952	1.876	1.592	1.34	1.143	0.4809

1968	1.176	1.128	0.9564	0.7444	0.6382	0.2554

1969	1.641	1.583	1.39	1.165	1.033	0.407

1970	2.673	2.572	2.382	1.845	1.524	0.597

1971	0.8983	0.8674	0.7374	0.5635	0.4665	0.2417

1972	1.144	1.098	0.9347	0.7631	0.7171	0.2905

1973	0.847	0.8151	0.7179	0.5996	0.5369	0.2247

1974	1.628	1.558	1.306	0.9668	0.8058	0.3301

1975	0.5509	0.5285	0.4482	0.3331	0.2735	0.1611

1976	2.65	2.555	2.266	1.668	1.37	0.5002

1977	1.654	1.587	1.46	1.17	0.962	0.396

1978	0.8772	0.8431	0.7262	0.5754	0.4826	0.1822

1979	4.03	3.86	3.265	2.364	1.909	0.6883

1980	1.775	1.703	1.484	1.132	0.9456	0.3614

1981	1.651	1.582	1.333	1.012	0.8467	0.3175

1982	1.94	1.861	1.63	1.353	1.137	0.4349

1983	1.979	1.912	1.757	1.345	1.122	0.3937

1984	3.769	3.617	3.07	2.379	2.011	0.7126

1985	2.194	2.1	1.765	1.484	1.257	0.4856

1986	1.346	1.292	1.164	0.9305	0.8126	0.3166

1987	2.125	2.042	1.873	1.415	1.156	0.4231

1988	0.8595	0.8261	0.7485	0.6793	0.609	0.239

1989	1.105	1.081	0.9269	0.6584	0.5858	0.2607

1990	1.07	1.024	0.8643	0.6427	0.5633	0.2283

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	4.861	4.671	3.995	2.995	2.46	0.8862

0.0645161290322581	4.03	3.86	3.265	2.379	2.011	0.7126

0.0967741935483871	3.769	3.617	3.07	2.364	1.909	0.6883

0.129032258064516	2.673	2.572	2.382	1.845	1.524	0.597

0.161290322580645	2.65	2.555	2.266	1.668	1.37	0.5002

0.193548387096774	2.194	2.1	1.873	1.484	1.257	0.4856

0.225806451612903	2.125	2.042	1.765	1.415	1.156	0.4809

0.258064516129032	1.979	1.912	1.757	1.353	1.143	0.4349

0.290322580645161	1.952	1.876	1.63	1.345	1.137	0.4231

0.32258064516129	1.94	1.861	1.612	1.34	1.122	0.407

0.354838709677419	1.929	1.85	1.592	1.198	1.035	0.4031

0.387096774193548	1.775	1.703	1.484	1.17	1.033	0.396

0.419354838709677	1.654	1.587	1.46	1.165	0.962	0.3937

0.451612903225806	1.651	1.583	1.39	1.132	0.9456	0.3713

0.483870967741936	1.641	1.582	1.389	1.076	0.8949	0.3614

0.516129032258065	1.628	1.558	1.333	1.022	0.8514	0.3531

0.548387096774194	1.586	1.523	1.327	1.012	0.8467	0.3301

0.580645161290323	1.534	1.472	1.306	0.9668	0.8126	0.3175

0.612903225806452	1.346	1.292	1.164	0.9305	0.8058	0.3166

0.645161290322581	1.217	1.177	1.005	0.785	0.7171	0.2905

0.67741935483871	1.176	1.128	0.9564	0.7631	0.6706	0.2794

0.709677419354839	1.144	1.098	0.9347	0.7444	0.6382	0.2607

0.741935483870968	1.105	1.081	0.9269	0.6793	0.609	0.2554

0.774193548387097	1.07	1.024	0.8643	0.6584	0.5858	0.2431

0.806451612903226	0.8983	0.8674	0.7485	0.6427	0.5633	0.2417

0.838709677419355	0.8772	0.8431	0.7374	0.5996	0.5369	0.239

0.870967741935484	0.8595	0.8261	0.7262	0.5754	0.4826	0.2283

0.903225806451613	0.847	0.8151	0.7179	0.5635	0.4665	0.2247

0.935483870967742	0.8275	0.7959	0.6812	0.5225	0.4605	0.1822

0.967741935483871	0.5509	0.5285	0.4482	0.3331	0.2735	0.1611

0.1	3.6594	3.5125	3.0012	2.3121	1.8705	0.67917

					Average of yearly averages:	0.382156666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: FLTOMAIR

Metfile:	w12844.dvf

PRZM scenario:	FLtomatoSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1098	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.05	fraction of application rate applied to pond

Application Date	Date	1-2	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	5	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1098	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

stored as FLTOMGRD.out

Chemical: DPXE2Y45

PRZM environment: FLtomatoSTD.txt	modified Tueday, 29 May 2007 at
12:54:10

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w12844.dvf	modified Wedday, 3 July 2002 at 09:04:30

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	1.434	1.374	1.283	0.9973	0.8287	0.2941

1962	1.484	1.423	1.239	0.9516	0.7921	0.3129

1963	0.691	0.6692	0.5747	0.424	0.3485	0.1772

1964	1.576	1.538	1.327	0.9841	0.8619	0.343

1965	0.9527	0.9222	0.7872	0.5688	0.4807	0.2164

1966	4.746	4.56	3.894	2.921	2.398	0.8443

1967	1.711	1.643	1.392	1.201	1.032	0.4259

1968	0.9146	0.8772	0.7418	0.5602	0.4681	0.1904

1969	1.465	1.412	1.239	0.9861	0.8869	0.3438

1970	2.547	2.45	2.267	1.761	1.451	0.5431

1971	0.8616	0.8304	0.703	0.5344	0.4398	0.1786

1972	0.7846	0.7529	0.6395	0.5522	0.5461	0.2268

1973	0.5384	0.5177	0.4434	0.3972	0.3582	0.1559

1974	1.492	1.426	1.192	0.8806	0.734	0.2717

1975	0.398	0.3815	0.3389	0.2576	0.2145	0.09435

1976	2.488	2.394	2.132	1.563	1.283	0.4476

1977	1.639	1.571	1.442	1.156	0.9484	0.3377

1978	0.4972	0.4782	0.4097	0.3389	0.2856	0.1145

1979	4.094	3.92	3.311	2.391	1.929	0.6441

1980	1.581	1.516	1.298	0.9959	0.8245	0.3029

1981	1.385	1.326	1.116	0.856	0.7025	0.2583

1982	1.797	1.723	1.512	1.254	1.055	0.3794

1983	1.699	1.632	1.514	1.166	0.9583	0.3358

1984	3.535	3.392	2.878	2.247	1.908	0.6688

1985	2.103	2.011	1.686	1.431	1.213	0.4345

1986	1.177	1.129	1.025	0.805	0.6837	0.259

1987	1.963	1.885	1.741	1.318	1.075	0.3667

1988	0.6825	0.6553	0.5862	0.4917	0.4369	0.1757

1989	1.039	1.014	0.8669	0.6108	0.4944	0.2025

1990	0.8114	0.7761	0.6527	0.4824	0.4062	0.1659

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	4.746	4.56	3.894	2.921	2.398	0.8443

0.0645161290322581	4.094	3.92	3.311	2.391	1.929	0.6688

0.0967741935483871	3.535	3.392	2.878	2.247	1.908	0.6441

0.129032258064516	2.547	2.45	2.267	1.761	1.451	0.5431

0.161290322580645	2.488	2.394	2.132	1.563	1.283	0.4476

0.193548387096774	2.103	2.011	1.741	1.431	1.213	0.4345

0.225806451612903	1.963	1.885	1.686	1.318	1.075	0.4259

0.258064516129032	1.797	1.723	1.514	1.254	1.055	0.3794

0.290322580645161	1.711	1.643	1.512	1.201	1.032	0.3667

0.32258064516129	1.699	1.632	1.442	1.166	0.9583	0.3438

0.354838709677419	1.639	1.571	1.392	1.156	0.9484	0.343

0.387096774193548	1.581	1.538	1.327	0.9973	0.8869	0.3377

0.419354838709677	1.576	1.516	1.298	0.9959	0.8619	0.3358

0.451612903225806	1.492	1.426	1.283	0.9861	0.8287	0.3129

0.483870967741936	1.484	1.423	1.239	0.9841	0.8245	0.3029

0.516129032258065	1.465	1.412	1.239	0.9516	0.7921	0.2941

0.548387096774194	1.434	1.374	1.192	0.8806	0.734	0.2717

0.580645161290323	1.385	1.326	1.116	0.856	0.7025	0.259

0.612903225806452	1.177	1.129	1.025	0.805	0.6837	0.2583

0.645161290322581	1.039	1.014	0.8669	0.6108	0.5461	0.2268

0.67741935483871	0.9527	0.9222	0.7872	0.5688	0.4944	0.2164

0.709677419354839	0.9146	0.8772	0.7418	0.5602	0.4807	0.2025

0.741935483870968	0.8616	0.8304	0.703	0.5522	0.4681	0.1904

0.774193548387097	0.8114	0.7761	0.6527	0.5344	0.4398	0.1786

0.806451612903226	0.7846	0.7529	0.6395	0.4917	0.4369	0.1772

0.838709677419355	0.691	0.6692	0.5862	0.4824	0.4062	0.1757

0.870967741935484	0.6825	0.6553	0.5747	0.424	0.3582	0.1659

0.903225806451613	0.5384	0.5177	0.4434	0.3972	0.3485	0.1559

0.935483870967742	0.4972	0.4782	0.4097	0.3389	0.2856	0.1145

0.967741935483871	0.398	0.3815	0.3389	0.2576	0.2145	0.09435

0.1	3.4362	3.2978	2.8169	2.1984	1.8623	0.634

					Average of yearly averages:	0.323728333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: FLTOMGRD

Metfile:	w12844.dvf

PRZM scenario:	FLtomatoSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1098	kg/ha

Application Efficiency:	APPEFF	0.99	fraction

Spray Drift	DRFT	0.01	fraction of application rate applied to pond

Application Date	Date	1-2	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	5	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1098	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

FL Turf

stored as FLTURFGRD.out

Chemical: DPXE2Y45

PRZM environment: FLturfSTD.txt	modified Tueday, 21 February 2006 at
14:38:26

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w12834.dvf	modified Wedday, 3 July 2002 at 09:04:28

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.3042	0.292	0.248	0.184	0.1522	0.05619

1962	0.2756	0.2644	0.224	0.1687	0.1403	0.0804

1963	0.3138	0.302	0.2591	0.1966	0.1632	0.06292

1964	0.2777	0.2672	0.2289	0.1733	0.1509	0.07009

1965	0.2786	0.2679	0.2292	0.1743	0.1456	0.05886

1966	0.2787	0.2685	0.2442	0.2043	0.1995	0.08819

1967	0.28	0.269	0.2291	0.1719	0.1421	0.06219

1968	0.2937	0.283	0.2478	0.1849	0.1524	0.09058

1969	0.2852	0.2744	0.2354	0.1801	0.151	0.06719

1970	0.3967	0.3813	0.3256	0.2513	0.21	0.07387

1971	1.286	1.232	1.04	0.7549	0.6394	0.231

1972	0.3977	0.382	0.3253	0.241	0.2269	0.1013

1973	0.2814	0.2702	0.23	0.174	0.1448	0.05184

1974	0.2737	0.2622	0.2209	0.1647	0.1359	0.04858

1975	0.2749	0.264	0.2247	0.1682	0.1516	0.05927

1976	1.351	1.292	1.08	0.7859	0.648	0.2463

1977	0.328	0.3153	0.2695	0.2058	0.1704	0.07419

1978	0.3865	0.3718	0.3196	0.2377	0.2132	0.08487

1979	0.4489	0.43	0.3653	0.2801	0.2462	0.09866

1980	0.2803	0.2697	0.2313	0.1754	0.1476	0.05238

1981	0.8062	0.7737	0.6558	0.4731	0.3945	0.1383

1982	0.3456	0.3324	0.2848	0.2089	0.2055	0.09071

1983	0.4123	0.3967	0.3593	0.3184	0.2835	0.1045

1984	0.5425	0.5202	0.4403	0.3359	0.2939	0.1382

1985	0.2841	0.2727	0.2318	0.173	0.1472	0.05542

1986	0.2749	0.2637	0.2236	0.1665	0.1364	0.05373

1987	0.8409	0.8089	0.7123	0.5376	0.444	0.1532

1988	0.2814	0.2702	0.2295	0.1735	0.1439	0.05056

1989	0.2724	0.2605	0.2179	0.1616	0.134	0.05133

1990	0.7528	0.7275	0.6182	0.4394	0.3664	0.13

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	1.351	1.292	1.08	0.7859	0.648	0.2463

0.0645161290322581	1.286	1.232	1.04	0.7549	0.6394	0.231

0.0967741935483871	0.8409	0.8089	0.7123	0.5376	0.444	0.1532

0.129032258064516	0.8062	0.7737	0.6558	0.4731	0.3945	0.1383

0.161290322580645	0.7528	0.7275	0.6182	0.4394	0.3664	0.1382

0.193548387096774	0.5425	0.5202	0.4403	0.3359	0.2939	0.13

0.225806451612903	0.4489	0.43	0.3653	0.3184	0.2835	0.1045

0.258064516129032	0.4123	0.3967	0.3593	0.2801	0.2462	0.1013

0.290322580645161	0.3977	0.382	0.3256	0.2513	0.2269	0.09866

0.32258064516129	0.3967	0.3813	0.3253	0.241	0.2132	0.09071

0.354838709677419	0.3865	0.3718	0.3196	0.2377	0.21	0.09058

0.387096774193548	0.3456	0.3324	0.2848	0.2089	0.2055	0.08819

0.419354838709677	0.328	0.3153	0.2695	0.2058	0.1995	0.08487

0.451612903225806	0.3138	0.302	0.2591	0.2043	0.1704	0.0804

0.483870967741936	0.3042	0.292	0.248	0.1966	0.1632	0.07419

0.516129032258065	0.2937	0.283	0.2478	0.1849	0.1524	0.07387

0.548387096774194	0.2852	0.2744	0.2442	0.184	0.1522	0.07009

0.580645161290323	0.2841	0.2727	0.2354	0.1801	0.1516	0.06719

0.612903225806452	0.2814	0.2702	0.2318	0.1754	0.151	0.06292

0.645161290322581	0.2814	0.2702	0.2313	0.1743	0.1509	0.06219

0.67741935483871	0.2803	0.2697	0.23	0.174	0.1476	0.05927

0.709677419354839	0.28	0.269	0.2295	0.1735	0.1472	0.05886

0.741935483870968	0.2787	0.2685	0.2292	0.1733	0.1456	0.05619

0.774193548387097	0.2786	0.2679	0.2291	0.173	0.1448	0.05542

0.806451612903226	0.2777	0.2672	0.2289	0.1719	0.1439	0.05373

0.838709677419355	0.2756	0.2644	0.2247	0.1687	0.1421	0.05238

0.870967741935484	0.2749	0.264	0.224	0.1682	0.1403	0.05184

0.903225806451613	0.2749	0.2637	0.2236	0.1665	0.1364	0.05133

0.935483870967742	0.2737	0.2622	0.2209	0.1647	0.1359	0.05056

0.967741935483871	0.2724	0.2605	0.2179	0.1616	0.134	0.04858

0.1	0.83743	0.80538	0.70665	0.53115	0.43905	0.15171

					Average of yearly averages:	0.0908273333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: FLTURFGRD

Metfile:	w12834.dvf

PRZM scenario:	FLturfSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.2912	kg/ha

Application Efficiency:	APPEFF	0.99	fraction

Spray Drift	DRFT	0.01	fraction of application rate applied to pond

Application Date	Date	1-2	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	7	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.2912	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

stored as FLTF19GRD.out

Chemical: DPXE2Y45

PRZM environment: FLturfSTD.txt	modified Tueday, 21 February 2006 at
13:38:26

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
15:33:30

Metfile: w12834.dvf	modified Wedday, 3 July 2002 at 08:04:28

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.2069	0.1995	0.1706	0.1294	0.1186	0.06416

1962	0.3577	0.3443	0.2956	0.2465	0.2082	0.09847

1963	0.4252	0.4087	0.3514	0.2613	0.2306	0.1115

1964	0.415	0.3984	0.3584	0.2845	0.2708	0.126

1965	0.2586	0.249	0.2176	0.17	0.1478	0.07985

1966	0.5722	0.5517	0.5084	0.4391	0.3785	0.1814

1967	0.2199	0.2123	0.1941	0.1543	0.1386	0.08019

1968	0.7728	0.7506	0.659	0.4937	0.4052	0.1595

1969	0.2794	0.2721	0.2397	0.2093	0.1799	0.09624

1970	0.1152	0.1112	0.1073	0.1049	0.1017	0.05311

1971	0.305	0.2939	0.2539	0.2153	0.2037	0.1164

1972	0.5046	0.4836	0.4246	0.3401	0.3216	0.1547

1973	0.1162	0.1124	0.108	0.1041	0.1005	0.0555

1974	0.1137	0.1098	0.1032	0.09852	0.09491	0.05044

1975	0.1388	0.1333	0.1268	0.1226	0.1156	0.05526

1976	1.013	0.9679	0.8226	0.646	0.5972	0.2292

1977	0.1971	0.1893	0.176	0.1373	0.1284	0.08563

1978	0.4537	0.4398	0.38	0.3111	0.2791	0.117

1979	0.4116	0.4017	0.3548	0.2755	0.2525	0.1202

1980	0.1129	0.1088	0.1051	0.1019	0.0987	0.05299

1981	0.159	0.1527	0.1459	0.1344	0.1291	0.06668

1982	0.5367	0.5149	0.4547	0.3565	0.3437	0.1504

1983	0.495	0.4758	0.4091	0.3247	0.2723	0.1407

1984	1.095	1.06	0.9081	0.6616	0.5415	0.2354

1985	0.16	0.1542	0.1329	0.1198	0.1175	0.06582

1986	0.1616	0.1552	0.1349	0.1116	0.1053	0.06136

1987	0.1791	0.1726	0.1599	0.1439	0.1353	0.066

1988	0.1073	0.1034	0.09857	0.09406	0.08995	0.04502

1989	0.1393	0.1334	0.1267	0.1146	0.1038	0.05085

1990	0.193	0.1865	0.1715	0.151	0.1417	0.0654

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	1.095	1.06	0.9081	0.6616	0.5972	0.2354

0.0645161290322581	1.013	0.9679	0.8226	0.646	0.5415	0.2292

0.0967741935483871	0.7728	0.7506	0.659	0.4937	0.4052	0.1814

0.129032258064516	0.5722	0.5517	0.5084	0.4391	0.3785	0.1595

0.161290322580645	0.5367	0.5149	0.4547	0.3565	0.3437	0.1547

0.193548387096774	0.5046	0.4836	0.4246	0.3401	0.3216	0.1504

0.225806451612903	0.495	0.4758	0.4091	0.3247	0.2791	0.1407

0.258064516129032	0.4537	0.4398	0.38	0.3111	0.2723	0.126

0.290322580645161	0.4252	0.4087	0.3584	0.2845	0.2708	0.1202

0.32258064516129	0.415	0.4017	0.3548	0.2755	0.2525	0.117

0.354838709677419	0.4116	0.3984	0.3514	0.2613	0.2306	0.1164

0.387096774193548	0.3577	0.3443	0.2956	0.2465	0.2082	0.1115

0.419354838709677	0.305	0.2939	0.2539	0.2153	0.2037	0.09847

0.451612903225806	0.2794	0.2721	0.2397	0.2093	0.1799	0.09624

0.483870967741936	0.2586	0.249	0.2176	0.17	0.1478	0.08563

0.516129032258065	0.2199	0.2123	0.1941	0.1543	0.1417	0.08019

0.548387096774194	0.2069	0.1995	0.176	0.151	0.1386	0.07985

0.580645161290323	0.1971	0.1893	0.1715	0.1439	0.1353	0.06668

0.612903225806452	0.193	0.1865	0.1706	0.1373	0.1291	0.066

0.645161290322581	0.1791	0.1726	0.1599	0.1344	0.1284	0.06582

0.67741935483871	0.1616	0.1552	0.1459	0.1294	0.1186	0.0654

0.709677419354839	0.16	0.1542	0.1349	0.1226	0.1175	0.06416

0.741935483870968	0.159	0.1527	0.1329	0.1198	0.1156	0.06136

0.774193548387097	0.1393	0.1334	0.1268	0.1146	0.1053	0.0555

0.806451612903226	0.1388	0.1333	0.1267	0.1116	0.1038	0.05526

0.838709677419355	0.1162	0.1124	0.108	0.1049	0.1017	0.05311

0.870967741935484	0.1152	0.1112	0.1073	0.1041	0.1005	0.05299

0.903225806451613	0.1137	0.1098	0.1051	0.1019	0.0987	0.05085

0.935483870967742	0.1129	0.1088	0.1032	0.09852	0.09491	0.05044

0.967741935483871	0.1073	0.1034	0.09857	0.09406	0.08995	0.04502

0.1	0.75274	0.73071	0.64394	0.48824	0.40253	0.17921

					Average of yearly averages:	0.101179

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: FLTF19GRD

Metfile:	w12834.dvf

PRZM scenario:	FLturfSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.029	kg/ha

Application Efficiency:	APPEFF	0.99	fraction

Spray Drift	DRFT	0.01	fraction of application rate applied to pond

Application Date	Date	1-2	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	7	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.029	kg/ha

Interval 2	interval	7	days	Set to 0 or delete line for single app.

app. rate 2	apprate	0.029	kg/ha

Interval 3	interval	7	days	Set to 0 or delete line for single app.

app. rate 3	apprate	0.029	kg/ha

Interval 4	interval	7	days	Set to 0 or delete line for single app.

app. rate 4	apprate	0.029	kg/ha

Interval 5	interval	7	days	Set to 0 or delete line for single app.

app. rate 5	apprate	0.029	kg/ha

Interval 6	interval	7	days	Set to 0 or delete line for single app.

app. rate 6	apprate	0.029	kg/ha

Interval 7	interval	7	days	Set to 0 or delete line for single app.

app. rate 7	apprate	0.029	kg/ha

Interval 8	interval	7	days	Set to 0 or delete line for single app.

app. rate 8	apprate	0.029	kg/ha

Interval 9	interval	7	days	Set to 0 or delete line for single app.

app. rate 9	apprate	0.029	kg/ha

Interval 10	interval	7	days	Set to 0 or delete line for single app.

app. rate 10	apprate	0.029	kg/ha

Interval 11	interval	7	days	Set to 0 or delete line for single app.

app. rate 11	apprate	0.029	kg/ha

Interval 12	interval	7	days	Set to 0 or delete line for single app.

app. rate 12	apprate	0.029	kg/ha

Interval 13	interval	7	days	Set to 0 or delete line for single app.

app. rate 13	apprate	0.029	kg/ha

Interval 14	interval	7	days	Set to 0 or delete line for single app.

app. rate 14	apprate	0.029	kg/ha

Interval 15	interval	7	days	Set to 0 or delete line for single app.

app. rate 15	apprate	0.029	kg/ha

Interval 16	interval	7	days	Set to 0 or delete line for single app.

app. rate 16	apprate	0.029	kg/ha

Interval 17	interval	7	days	Set to 0 or delete line for single app.

app. rate 17	apprate	0.029	kg/ha

Interval 18	interval	7	days	Set to 0 or delete line for single app.

app. rate 18	apprate	0.029	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

GA Peach

stored as GAPEACHAIR.out

Chemical: DPXE2Y45

PRZM environment: GAPeachesSTD.txt	modified Tueday, 29 May 2007 at
12:54:56

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w03813.dvf	modified Wedday, 3 July 2002 at 09:04:32

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.5362	0.5148	0.4376	0.3302	0.2745	0.09233

1962	0.8173	0.7837	0.6708	0.517	0.4537	0.1685

1963	0.5601	0.5383	0.4606	0.4085	0.3523	0.1324

1964	1.243	1.191	1.056	0.7884	0.6506	0.2286

1965	0.5353	0.5123	0.4303	0.3303	0.2811	0.111

1966	0.6999	0.6747	0.587	0.4515	0.3784	0.1355

1967	0.5879	0.5638	0.4773	0.4116	0.3565	0.1334

1968	1.116	1.071	0.9094	0.6699	0.5576	0.201

1969	0.5378	0.5173	0.4434	0.3341	0.2775	0.1066

1970	0.5252	0.5039	0.4273	0.3214	0.2674	0.09638

1971	0.7467	0.7165	0.6079	0.4684	0.3957	0.1441

1972	0.5332	0.5134	0.4417	0.3393	0.2879	0.1073

1973	0.6639	0.6385	0.5482	0.459	0.3982	0.1472

1974	0.6317	0.6073	0.5189	0.434	0.3709	0.138

1975	0.5502	0.5288	0.4597	0.3494	0.2933	0.1089

1976	2.06	1.999	1.721	1.263	1.033	0.3588

1977	0.5491	0.5269	0.4469	0.3349	0.2763	0.1149

1978	0.5308	0.5097	0.4339	0.324	0.2683	0.09541

1979	0.5631	0.5416	0.4852	0.3663	0.3074	0.1102

1980	0.5265	0.5053	0.4293	0.3206	0.2638	0.09269

1981	0.7037	0.6745	0.5702	0.4571	0.4063	0.1523

1982	0.5306	0.5085	0.4333	0.3256	0.2713	0.1018

1983	0.5239	0.5023	0.4246	0.3759	0.3276	0.1183

1984	0.6495	0.6231	0.524	0.4403	0.3783	0.137

1985	0.5266	0.5046	0.4261	0.3175	0.2627	0.09595

1986	0.5218	0.4998	0.4213	0.3122	0.2557	0.08914

1987	0.5235	0.5022	0.4319	0.3244	0.2682	0.09282

1988	0.5194	0.4963	0.414	0.3035	0.2496	0.08741

1989	0.7574	0.7261	0.6221	0.4661	0.3887	0.1362

1990	0.5269	0.5105	0.4331	0.3211	0.2637	0.09329

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	2.06	1.999	1.721	1.263	1.033	0.3588

0.0645161290322581	1.243	1.191	1.056	0.7884	0.6506	0.2286

0.0967741935483871	1.116	1.071	0.9094	0.6699	0.5576	0.201

0.129032258064516	0.8173	0.7837	0.6708	0.517	0.4537	0.1685

0.161290322580645	0.7574	0.7261	0.6221	0.4684	0.4063	0.1523

0.193548387096774	0.7467	0.7165	0.6079	0.4661	0.3982	0.1472

0.225806451612903	0.7037	0.6747	0.587	0.459	0.3957	0.1441

0.258064516129032	0.6999	0.6745	0.5702	0.4571	0.3887	0.138

0.290322580645161	0.6639	0.6385	0.5482	0.4515	0.3784	0.137

0.32258064516129	0.6495	0.6231	0.524	0.4403	0.3783	0.1362

0.354838709677419	0.6317	0.6073	0.5189	0.434	0.3709	0.1355

0.387096774193548	0.5879	0.5638	0.4852	0.4116	0.3565	0.1334

0.419354838709677	0.5631	0.5416	0.4773	0.4085	0.3523	0.1324

0.451612903225806	0.5601	0.5383	0.4606	0.3759	0.3276	0.1183

0.483870967741936	0.5502	0.5288	0.4597	0.3663	0.3074	0.1149

0.516129032258065	0.5491	0.5269	0.4469	0.3494	0.2933	0.111

0.548387096774194	0.5378	0.5173	0.4434	0.3393	0.2879	0.1102

0.580645161290323	0.5362	0.5148	0.4417	0.3349	0.2811	0.1089

0.612903225806452	0.5353	0.5134	0.4376	0.3341	0.2775	0.1073

0.645161290322581	0.5332	0.5123	0.4339	0.3303	0.2763	0.1066

0.67741935483871	0.5308	0.5105	0.4333	0.3302	0.2745	0.1018

0.709677419354839	0.5306	0.5097	0.4331	0.3256	0.2713	0.09638

0.741935483870968	0.5269	0.5085	0.4319	0.3244	0.2683	0.09595

0.774193548387097	0.5266	0.5053	0.4303	0.324	0.2682	0.09541

0.806451612903226	0.5265	0.5046	0.4293	0.3214	0.2674	0.09329

0.838709677419355	0.5252	0.5039	0.4273	0.3211	0.2638	0.09282

0.870967741935484	0.5239	0.5023	0.4261	0.3206	0.2637	0.09269

0.903225806451613	0.5235	0.5022	0.4246	0.3175	0.2627	0.09233

0.935483870967742	0.5218	0.4998	0.4213	0.3122	0.2557	0.08914

0.967741935483871	0.5194	0.4963	0.414	0.3035	0.2496	0.08741

0.1	1.08613	1.04227	0.88554	0.65461	0.54721	0.19775

					Average of yearly averages:	0.130914

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: GAPEACHAIR

Metfile:	w03813.dvf

PRZM scenario:	GAPeachesSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1109	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.05	fraction of application rate applied to pond

Application Date	Date	1-5	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	7	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1109	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

stored as GAPEACHGRD.out

Chemical: DPXE2Y45

PRZM environment: GAPeachesSTD.txt	modified Tueday, 29 May 2007 at
12:54:56

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w03813.dvf	modified Wedday, 3 July 2002 at 09:04:32

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.1237	0.1187	0.101	0.07746	0.06444	0.02168

1962	0.5923	0.5672	0.4827	0.3521	0.2873	0.1003

1963	0.2909	0.2792	0.2375	0.1742	0.1474	0.05991

1964	0.9096	0.8712	0.7674	0.5572	0.4578	0.1582

1965	0.1179	0.1131	0.09579	0.07907	0.07049	0.03472

1966	0.3234	0.3116	0.2728	0.1993	0.1641	0.05807

1967	0.2504	0.2411	0.2075	0.1642	0.1473	0.05741

1968	0.7817	0.7498	0.6355	0.458	0.3742	0.13

1969	0.1171	0.1128	0.09753	0.07509	0.0631	0.03013

1970	0.1055	0.1012	0.08597	0.06548	0.05464	0.02

1971	0.3967	0.3804	0.3217	0.2332	0.1927	0.06877

1972	0.111	0.107	0.0924	0.07774	0.07032	0.03005

1973	0.399	0.3831	0.3267	0.2399	0.1969	0.07199

1974	0.3314	0.3183	0.2706	0.1976	0.1645	0.06339

1975	0.1305	0.1255	0.116	0.09091	0.07718	0.03078

1976	1.761	1.704	1.469	1.075	0.877	0.2923

1977	0.1316	0.1267	0.1091	0.08459	0.07067	0.04266

1978	0.1113	0.1069	0.09108	0.06788	0.05649	0.02066

1979	0.1777	0.1708	0.146	0.1094	0.09141	0.03265

1980	0.1064	0.1021	0.08685	0.0651	0.05372	0.01961

1981	0.4944	0.4729	0.3971	0.2837	0.2316	0.08282

1982	0.113	0.1085	0.09641	0.07473	0.06289	0.02776

1983	0.2442	0.2345	0.2007	0.1451	0.123	0.04639

1984	0.3881	0.3718	0.3108	0.2216	0.1828	0.068

1985	0.1094	0.1049	0.08892	0.06684	0.05552	0.02292

1986	0.1045	0.1001	0.08439	0.06257	0.05124	0.01797

1987	0.1047	0.1004	0.09168	0.07002	0.05858	0.02036

1988	0.1041	0.09943	0.08296	0.06083	0.05135	0.0185

1989	0.368	0.3527	0.2977	0.2195	0.1839	0.06352

1990	0.114	0.1097	0.09432	0.07011	0.05777	0.02246

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	1.761	1.704	1.469	1.075	0.877	0.2923

0.0645161290322581	0.9096	0.8712	0.7674	0.5572	0.4578	0.1582

0.0967741935483871	0.7817	0.7498	0.6355	0.458	0.3742	0.13

0.129032258064516	0.5923	0.5672	0.4827	0.3521	0.2873	0.1003

0.161290322580645	0.4944	0.4729	0.3971	0.2837	0.2316	0.08282

0.193548387096774	0.399	0.3831	0.3267	0.2399	0.1969	0.07199

0.225806451612903	0.3967	0.3804	0.3217	0.2332	0.1927	0.06877

0.258064516129032	0.3881	0.3718	0.3108	0.2216	0.1839	0.068

0.290322580645161	0.368	0.3527	0.2977	0.2195	0.1828	0.06352

0.32258064516129	0.3314	0.3183	0.2728	0.1993	0.1645	0.06339

0.354838709677419	0.3234	0.3116	0.2706	0.1976	0.1641	0.05991

0.387096774193548	0.2909	0.2792	0.2375	0.1742	0.1474	0.05807

0.419354838709677	0.2504	0.2411	0.2075	0.1642	0.1473	0.05741

0.451612903225806	0.2442	0.2345	0.2007	0.1451	0.123	0.04639

0.483870967741936	0.1777	0.1708	0.146	0.1094	0.09141	0.04266

0.516129032258065	0.1316	0.1267	0.116	0.09091	0.07718	0.03472

0.548387096774194	0.1305	0.1255	0.1091	0.08459	0.07067	0.03265

0.580645161290323	0.1237	0.1187	0.101	0.07907	0.07049	0.03078

0.612903225806452	0.1179	0.1131	0.09753	0.07774	0.07032	0.03013

0.645161290322581	0.1171	0.1128	0.09641	0.07746	0.06444	0.03005

0.67741935483871	0.114	0.1097	0.09579	0.07509	0.0631	0.02776

0.709677419354839	0.113	0.1085	0.09432	0.07473	0.06289	0.02292

0.741935483870968	0.1113	0.107	0.0924	0.07011	0.05858	0.02246

0.774193548387097	0.111	0.1069	0.09168	0.07002	0.05777	0.02168

0.806451612903226	0.1094	0.1049	0.09108	0.06788	0.05649	0.02066

0.838709677419355	0.1064	0.1021	0.08892	0.06684	0.05552	0.02036

0.870967741935484	0.1055	0.1012	0.08685	0.06548	0.05464	0.02

0.903225806451613	0.1047	0.1004	0.08597	0.0651	0.05372	0.01961

0.935483870967742	0.1045	0.1001	0.08439	0.06257	0.05135	0.0185

0.967741935483871	0.1041	0.09943	0.08296	0.06083	0.05124	0.01797

0.1	0.76276	0.73154	0.62022	0.44741	0.36551	0.12703

					Average of yearly averages:	0.0577993333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: GAPEACHGRD

Metfile:	w03813.dvf

PRZM scenario:	GAPeachesSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1109	kg/ha

Application Efficiency:	APPEFF	0.99	fraction

Spray Drift	DRFT	0.01	fraction of application rate applied to pond

Application Date	Date	1-5	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	7	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1109	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

ID Potato

stored as IDPOTAIR.out

Chemical: DPXE2Y45

PRZM environment: IDNpotato_WirrigSTD.txt	modified Tueday, 29 May 2007
at 12:55:22

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w24156.dvf	modified Wedday, 3 July 2002 at 09:04:38

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.5304	0.5133	0.45	0.4127	0.3814	0.151

1962	0.5702	0.5503	0.478	0.3766	0.323	0.1362

1963	0.8465	0.8218	0.7477	0.6448	0.5756	0.231

1964	0.6386	0.619	0.55	0.5136	0.4575	0.1983

1965	0.5788	0.5611	0.496	0.3932	0.3376	0.1459

1966	0.5614	0.5422	0.472	0.3978	0.3499	0.1494

1967	0.5895	0.5708	0.5245	0.4788	0.4367	0.1836

1968	0.5653	0.5465	0.4779	0.4025	0.378	0.1683

1969	0.5915	0.5711	0.4967	0.3833	0.3733	0.185

1970	1.075	1.039	0.9097	0.7119	0.6025	0.28

1971	0.9403	0.9198	0.8144	0.6616	0.5852	0.2558

1972	0.8809	0.8547	0.7477	0.5844	0.4984	0.21

1973	0.5818	0.5628	0.4929	0.3835	0.3432	0.1589

1974	1.025	0.9908	0.8625	0.7789	0.7156	0.2956

1975	0.6148	0.5966	0.534	0.5009	0.4454	0.1988

1976	1.191	1.152	1.01	0.7617	0.6662	0.2707

1977	0.6051	0.588	0.5355	0.4667	0.4416	0.2022

1978	0.671	0.6503	0.5725	0.4732	0.4507	0.1969

1979	0.5907	0.5714	0.5006	0.3926	0.3342	0.1503

1980	0.5593	0.5399	0.4689	0.3983	0.357	0.1504

1981	0.7069	0.6861	0.6112	0.5212	0.4981	0.2128

1982	0.6613	0.6392	0.5741	0.4945	0.4356	0.1937

1983	0.58	0.5617	0.4942	0.4438	0.4018	0.1786

1984	0.9759	0.9449	0.8296	0.6558	0.5806	0.2411

1985	0.9184	0.8841	0.7763	0.6105	0.5167	0.2161

1986	0.6673	0.6456	0.5844	0.4699	0.4001	0.1657

1987	0.5536	0.5326	0.4566	0.3924	0.3546	0.1486

1988	0.5537	0.5346	0.4648	0.361	0.307	0.1233

1989	0.5543	0.5346	0.4631	0.3583	0.3095	0.1258

1990	0.5543	0.5351	0.4629	0.3637	0.3309	0.139

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	1.191	1.152	1.01	0.7789	0.7156	0.2956

0.0645161290322581	1.075	1.039	0.9097	0.7617	0.6662	0.28

0.0967741935483871	1.025	0.9908	0.8625	0.7119	0.6025	0.2707

0.129032258064516	0.9759	0.9449	0.8296	0.6616	0.5852	0.2558

0.161290322580645	0.9403	0.9198	0.8144	0.6558	0.5806	0.2411

0.193548387096774	0.9184	0.8841	0.7763	0.6448	0.5756	0.231

0.225806451612903	0.8809	0.8547	0.7477	0.6105	0.5167	0.2161

0.258064516129032	0.8465	0.8218	0.7477	0.5844	0.4984	0.2128

0.290322580645161	0.7069	0.6861	0.6112	0.5212	0.4981	0.21

0.32258064516129	0.671	0.6503	0.5844	0.5136	0.4575	0.2022

0.354838709677419	0.6673	0.6456	0.5741	0.5009	0.4507	0.1988

0.387096774193548	0.6613	0.6392	0.5725	0.4945	0.4454	0.1983

0.419354838709677	0.6386	0.619	0.55	0.4788	0.4416	0.1969

0.451612903225806	0.6148	0.5966	0.5355	0.4732	0.4367	0.1937

0.483870967741936	0.6051	0.588	0.534	0.4699	0.4356	0.185

0.516129032258065	0.5915	0.5714	0.5245	0.4667	0.4018	0.1836

0.548387096774194	0.5907	0.5711	0.5006	0.4438	0.4001	0.1786

0.580645161290323	0.5895	0.5708	0.4967	0.4127	0.3814	0.1683

0.612903225806452	0.5818	0.5628	0.496	0.4025	0.378	0.1657

0.645161290322581	0.58	0.5617	0.4942	0.3983	0.3733	0.1589

0.67741935483871	0.5788	0.5611	0.4929	0.3978	0.357	0.151

0.709677419354839	0.5702	0.5503	0.478	0.3932	0.3546	0.1504

0.741935483870968	0.5653	0.5465	0.4779	0.3926	0.3499	0.1503

0.774193548387097	0.5614	0.5422	0.472	0.3924	0.3432	0.1494

0.806451612903226	0.5593	0.5399	0.4689	0.3835	0.3376	0.1486

0.838709677419355	0.5543	0.5351	0.4648	0.3833	0.3342	0.1459

0.870967741935484	0.5543	0.5346	0.4631	0.3766	0.3309	0.139

0.903225806451613	0.5537	0.5346	0.4629	0.3637	0.323	0.1362

0.935483870967742	0.5536	0.5326	0.4566	0.361	0.3095	0.1258

0.967741935483871	0.5304	0.5133	0.45	0.3583	0.307	0.1233

0.1	1.02009	0.98621	0.85921	0.70687	0.60077	0.26921

					Average of yearly averages:	0.188766666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: IDPOTAIR

Metfile:	w24156.dvf

PRZM scenario:	IDNpotato_WirrigSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.0739	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.05	fraction of application rate applied to pond

Application Date	Date	1-4	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	3	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.0739	kg/ha

Interval 2	interval	3	days	Set to 0 or delete line for single app.

app. rate 2	apprate	0.0739	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

stored as IDPOTGRD.out

Chemical: DPXE2Y45

PRZM environment: IDNpotato_WirrigSTD.txt	modified Tueday, 29 May 2007
at 12:55:22

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w24156.dvf	modified Wedday, 3 July 2002 at 09:04:38

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.3156	0.3047	0.2643	0.204	0.1704	0.06977

1962	0.1297	0.1254	0.1098	0.08802	0.07781	0.03973

1963	0.5369	0.5206	0.4815	0.3962	0.3378	0.135

1964	0.3396	0.3288	0.289	0.2314	0.2076	0.0987

1965	0.134	0.1301	0.1158	0.09306	0.08287	0.04402

1966	0.1763	0.1699	0.1468	0.1237	0.1117	0.0543

1967	0.3255	0.3145	0.2744	0.2309	0.2006	0.08584

1968	0.2231	0.2156	0.2003	0.1703	0.1445	0.07255

1969	0.3271	0.3162	0.2799	0.224	0.1867	0.08956

1970	0.8811	0.85	0.7403	0.5777	0.4803	0.1887

1971	0.6306	0.6144	0.5437	0.4194	0.3534	0.1599

1972	0.4799	0.4671	0.4086	0.3102	0.2632	0.115

1973	0.1752	0.1691	0.1511	0.1184	0.1021	0.06278

1974	0.8312	0.8024	0.6947	0.5238	0.5031	0.2068

1975	0.3296	0.3192	0.2807	0.2195	0.1975	0.1019

1976	0.9034	0.8729	0.7611	0.5684	0.474	0.1809

1977	0.3976	0.3856	0.3454	0.2731	0.2303	0.1121

1978	0.4498	0.4349	0.3793	0.2852	0.2357	0.1035

1979	0.1437	0.1394	0.1236	0.09925	0.08661	0.05064

1980	0.1708	0.1671	0.1534	0.1229	0.1119	0.05156

1981	0.4962	0.4805	0.4261	0.3222	0.2781	0.1174

1982	0.2916	0.2821	0.2473	0.217	0.1987	0.09701

1983	0.2345	0.2269	0.2115	0.1781	0.1564	0.07845

1984	0.6345	0.6138	0.5366	0.4151	0.357	0.1436

1985	0.4806	0.463	0.4286	0.3332	0.2827	0.1216

1986	0.2401	0.2326	0.2149	0.1837	0.1595	0.07051

1987	0.2261	0.2184	0.1967	0.1535	0.1295	0.06034

1988	0.1188	0.1148	0.1003	0.07867	0.07028	0.03437

1989	0.114	0.11	0.09546	0.07412	0.07115	0.03346

1990	0.1533	0.1477	0.1287	0.1073	0.0953	0.0469

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	0.9034	0.8729	0.7611	0.5777	0.5031	0.2068

0.0645161290322581	0.8811	0.85	0.7403	0.5684	0.4803	0.1887

0.0967741935483871	0.8312	0.8024	0.6947	0.5238	0.474	0.1809

0.129032258064516	0.6345	0.6144	0.5437	0.4194	0.357	0.1599

0.161290322580645	0.6306	0.6138	0.5366	0.4151	0.3534	0.1436

0.193548387096774	0.5369	0.5206	0.4815	0.3962	0.3378	0.135

0.225806451612903	0.4962	0.4805	0.4286	0.3332	0.2827	0.1216

0.258064516129032	0.4806	0.4671	0.4261	0.3222	0.2781	0.1174

0.290322580645161	0.4799	0.463	0.4086	0.3102	0.2632	0.115

0.32258064516129	0.4498	0.4349	0.3793	0.2852	0.2357	0.1121

0.354838709677419	0.3976	0.3856	0.3454	0.2731	0.2303	0.1035

0.387096774193548	0.3396	0.3288	0.289	0.2314	0.2076	0.1019

0.419354838709677	0.3296	0.3192	0.2807	0.2309	0.2006	0.0987

0.451612903225806	0.3271	0.3162	0.2799	0.224	0.1987	0.09701

0.483870967741936	0.3255	0.3145	0.2744	0.2195	0.1975	0.08956

0.516129032258065	0.3156	0.3047	0.2643	0.217	0.1867	0.08584

0.548387096774194	0.2916	0.2821	0.2473	0.204	0.1704	0.07845

0.580645161290323	0.2401	0.2326	0.2149	0.1837	0.1595	0.07255

0.612903225806452	0.2345	0.2269	0.2115	0.1781	0.1564	0.07051

0.645161290322581	0.2261	0.2184	0.2003	0.1703	0.1445	0.06977

0.67741935483871	0.2231	0.2156	0.1967	0.1535	0.1295	0.06278

0.709677419354839	0.1763	0.1699	0.1534	0.1237	0.1119	0.06034

0.741935483870968	0.1752	0.1691	0.1511	0.1229	0.1117	0.0543

0.774193548387097	0.1708	0.1671	0.1468	0.1184	0.1021	0.05156

0.806451612903226	0.1533	0.1477	0.1287	0.1073	0.0953	0.05064

0.838709677419355	0.1437	0.1394	0.1236	0.09925	0.08661	0.0469

0.870967741935484	0.134	0.1301	0.1158	0.09306	0.08287	0.04402

0.903225806451613	0.1297	0.1254	0.1098	0.08802	0.07781	0.03973

0.935483870967742	0.1188	0.1148	0.1003	0.07867	0.07115	0.03437

0.967741935483871	0.114	0.11	0.09546	0.07412	0.07028	0.03346

0.1	0.81153	0.7836	0.6796	0.51336	0.4623	0.1788

					Average of yearly averages:	0.0942296666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: IDPOTGRD

Metfile:	w24156.dvf

PRZM scenario:	IDNpotato_WirrigSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.0739	kg/ha

Application Efficiency:	APPEFF	0.99	fraction

Spray Drift	DRFT	0.01	fraction of application rate applied to pond

Application Date	Date	1-4	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	3	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.0739	kg/ha

Interval 2	interval	3	days	Set to 0 or delete line for single app.

app. rate 2	apprate	0.0739	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

MI Nursery

stored as MInursey.out

Chemical: DPXE2Y45

PRZM environment: MInurserySTD.txt	modified Wedday, 24 January 2007 at
09:17:52

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w14840.dvf	modified Wedday, 3 July 2002 at 09:05:38

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	1.4	1.359	1.245	1.12	0.998	0.5059

1962	1.112	1.101	1.013	0.9055	0.8346	0.4227

1963	2.017	1.964	1.789	1.504	1.365	0.6415

1964	0.8871	0.8672	0.8182	0.7761	0.7328	0.3946

1965	1.808	1.756	1.606	1.489	1.439	0.6982

1966	1.344	1.317	1.239	1.106	1.057	0.5308

1967	1.872	1.817	1.629	1.462	1.337	0.6372

1968	2.569	2.524	2.332	2.094	2.023	0.9688

1969	1.953	1.9	1.76	1.538	1.386	0.6641

1970	1.498	1.456	1.37	1.152	1.035	0.5365

1971	2.139	2.095	1.983	1.579	1.355	0.6412

1972	2.247	2.186	1.983	1.753	1.638	0.8035

1973	0.8999	0.8776	0.8246	0.7579	0.7444	0.465

1974	1.227	1.191	1.103	1.027	0.9687	0.5162

1975	0.8405	0.8359	0.7927	0.6986	0.6918	0.4157

1976	3.205	3.111	2.9	2.541	2.256	0.9482

1977	2.518	2.467	2.293	2.036	1.778	0.806

1978	2.419	2.351	2.198	1.834	1.655	0.7507

1979	2.414	2.352	2.188	2.008	1.869	0.8343

1980	1.892	1.838	1.648	1.357	1.2	0.5903

1981	2.042	1.987	1.8	1.498	1.305	0.6027

1982	2.198	2.135	2.04	1.871	1.73	0.815

1983	1.354	1.317	1.26	1.161	1.087	0.5589

1984	1.08	1.065	0.99	0.9319	0.8917	0.451

1985	1.201	1.181	1.121	1.004	0.9095	0.438

1986	1.171	1.137	1.087	1.034	1.002	0.5364

1987	1.116	1.087	1.031	0.9849	0.8962	0.4686

1988	0.9865	0.9554	0.9403	0.8969	0.8511	0.4509

1989	1.536	1.489	1.334	1.159	1.092	0.6157

1990	2.042	1.98	1.793	1.531	1.486	0.761

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	3.205	3.111	2.9	2.541	2.256	0.9688

0.0645161290322581	2.569	2.524	2.332	2.094	2.023	0.9482

0.0967741935483871	2.518	2.467	2.293	2.036	1.869	0.8343

0.129032258064516	2.419	2.352	2.198	2.008	1.778	0.815

0.161290322580645	2.414	2.351	2.188	1.871	1.73	0.806

0.193548387096774	2.247	2.186	2.04	1.834	1.655	0.8035

0.225806451612903	2.198	2.135	1.983	1.753	1.638	0.761

0.258064516129032	2.139	2.095	1.983	1.579	1.486	0.7507

0.290322580645161	2.042	1.987	1.8	1.538	1.439	0.6982

0.32258064516129	2.042	1.98	1.793	1.531	1.386	0.6641

0.354838709677419	2.017	1.964	1.789	1.504	1.365	0.6415

0.387096774193548	1.953	1.9	1.76	1.498	1.355	0.6412

0.419354838709677	1.892	1.838	1.648	1.489	1.337	0.6372

0.451612903225806	1.872	1.817	1.629	1.462	1.305	0.6157

0.483870967741936	1.808	1.756	1.606	1.357	1.2	0.6027

0.516129032258065	1.536	1.489	1.37	1.161	1.092	0.5903

0.548387096774194	1.498	1.456	1.334	1.159	1.087	0.5589

0.580645161290323	1.4	1.359	1.26	1.152	1.057	0.5365

0.612903225806452	1.354	1.317	1.245	1.12	1.035	0.5364

0.645161290322581	1.344	1.317	1.239	1.106	1.002	0.5308

0.67741935483871	1.227	1.191	1.121	1.034	0.998	0.5162

0.709677419354839	1.201	1.181	1.103	1.027	0.9687	0.5059

0.741935483870968	1.171	1.137	1.087	1.004	0.9095	0.4686

0.774193548387097	1.116	1.101	1.031	0.9849	0.8962	0.465

0.806451612903226	1.112	1.087	1.013	0.9319	0.8917	0.451

0.838709677419355	1.08	1.065	0.99	0.9055	0.8511	0.4509

0.870967741935484	0.9865	0.9554	0.9403	0.8969	0.8346	0.438

0.903225806451613	0.8999	0.8776	0.8246	0.7761	0.7444	0.4227

0.935483870967742	0.8871	0.8672	0.8182	0.7579	0.7328	0.4157

0.967741935483871	0.8405	0.8359	0.7927	0.6986	0.6918	0.3946

0.1	2.5081	2.4555	2.2835	2.0332	1.8599	0.83237

					Average of yearly averages:	0.615653333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: MInursey

Metfile:	w14840.dvf

PRZM scenario:	MInurserySTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.5591	kg/ha

Application Efficiency:	APPEFF	0.99	fraction

Spray Drift	DRFT	0.01	fraction of application rate applied to pond

Application Date	Date	1-2	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval		days	Set to 0 or delete line for single app.

app. rate 1	apprate		kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

MI Cherry

stored as MICHEAIR.out

Chemical: DPXE2Y45

PRZM environment: MICherriesSTD.txt	modified Tueday, 29 May 2007 at
12:56:56

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w14850.dvf	modified Wedday, 3 July 2002 at 09:05:40

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.5214	0.5033	0.4371	0.337	0.2905	0.1312

1962	0.6797	0.6581	0.5834	0.4971	0.4706	0.2338

1963	1.538	1.491	1.315	1.016	0.8609	0.3735

1964	0.6957	0.673	0.5898	0.4664	0.4356	0.2663

1965	0.6271	0.6072	0.5341	0.4273	0.3732	0.2176

1966	0.5993	0.5798	0.5084	0.3996	0.3447	0.2157

1967	0.7109	0.6878	0.6175	0.5089	0.4501	0.233

1968	0.587	0.5686	0.5006	0.405	0.3731	0.1892

1969	0.9807	0.9506	0.909	0.764	0.6584	0.3172

1970	0.665	0.6461	0.5759	0.4663	0.4101	0.2581

1971	0.6362	0.6155	0.5395	0.4281	0.37	0.2123

1972	0.6119	0.5912	0.5508	0.4466	0.4335	0.2369

1973	0.6115	0.5933	0.5266	0.4309	0.3913	0.2073

1974	0.6817	0.662	0.5936	0.5619	0.5057	0.2408

1975	0.6328	0.6116	0.5341	0.4601	0.402	0.232

1976	0.6129	0.5932	0.5208	0.4163	0.3562	0.199

1977	0.5765	0.5556	0.4797	0.4126	0.3668	0.202

1978	1.038	1.003	0.8867	0.7043	0.6067	0.2901

1979	0.7979	0.7737	0.6847	0.5705	0.5087	0.2772

1980	0.6363	0.6158	0.5406	0.4621	0.4219	0.2251

1981	0.7418	0.719	0.6526	0.5425	0.5071	0.2895

1982	1.005	0.9792	0.863	0.6746	0.582	0.3573

1983	0.9216	0.8943	0.8224	0.6703	0.6074	0.3286

1984	0.6535	0.6338	0.5614	0.4665	0.4133	0.2382

1985	0.8418	0.8134	0.7132	0.6115	0.549	0.314

1986	1.316	1.274	1.199	0.9566	0.8355	0.4567

1987	0.8883	0.8621	0.77	0.65	0.5824	0.3953

1988	0.7262	0.7025	0.6155	0.4908	0.435	0.2795

1989	0.9254	0.8971	0.7916	0.6856	0.625	0.3004

1990	0.6201	0.6097	0.5438	0.4931	0.4712	0.2556

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	1.538	1.491	1.315	1.016	0.8609	0.4567

0.0645161290322581	1.316	1.274	1.199	0.9566	0.8355	0.3953

0.0967741935483871	1.038	1.003	0.909	0.764	0.6584	0.3735

0.129032258064516	1.005	0.9792	0.8867	0.7043	0.625	0.3573

0.161290322580645	0.9807	0.9506	0.863	0.6856	0.6074	0.3286

0.193548387096774	0.9254	0.8971	0.8224	0.6746	0.6067	0.3172

0.225806451612903	0.9216	0.8943	0.7916	0.6703	0.5824	0.314

0.258064516129032	0.8883	0.8621	0.77	0.65	0.582	0.3004

0.290322580645161	0.8418	0.8134	0.7132	0.6115	0.549	0.2901

0.32258064516129	0.7979	0.7737	0.6847	0.5705	0.5087	0.2895

0.354838709677419	0.7418	0.719	0.6526	0.5619	0.5071	0.2795

0.387096774193548	0.7262	0.7025	0.6175	0.5425	0.5057	0.2772

0.419354838709677	0.7109	0.6878	0.6155	0.5089	0.4712	0.2663

0.451612903225806	0.6957	0.673	0.5936	0.4971	0.4706	0.2581

0.483870967741936	0.6817	0.662	0.5898	0.4931	0.4501	0.2556

0.516129032258065	0.6797	0.6581	0.5834	0.4908	0.4356	0.2408

0.548387096774194	0.665	0.6461	0.5759	0.4665	0.435	0.2382

0.580645161290323	0.6535	0.6338	0.5614	0.4664	0.4335	0.2369

0.612903225806452	0.6363	0.6158	0.5508	0.4663	0.4219	0.2338

0.645161290322581	0.6362	0.6155	0.5438	0.4621	0.4133	0.233

0.67741935483871	0.6328	0.6116	0.5406	0.4601	0.4101	0.232

0.709677419354839	0.6271	0.6097	0.5395	0.4466	0.402	0.2251

0.741935483870968	0.6201	0.6072	0.5341	0.4309	0.3913	0.2176

0.774193548387097	0.6129	0.5933	0.5341	0.4281	0.3732	0.2157

0.806451612903226	0.6119	0.5932	0.5266	0.4273	0.3731	0.2123

0.838709677419355	0.6115	0.5912	0.5208	0.4163	0.37	0.2073

0.870967741935484	0.5993	0.5798	0.5084	0.4126	0.3668	0.202

0.903225806451613	0.587	0.5686	0.5006	0.405	0.3562	0.199

0.935483870967742	0.5765	0.5556	0.4797	0.3996	0.3447	0.1892

0.967741935483871	0.5214	0.5033	0.4371	0.337	0.2905	0.1312

0.1	1.0347	1.00062	0.90677	0.75803	0.65506	0.37188

					Average of yearly averages:	0.26578

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: MICHEAIR

Metfile:	w14850.dvf

PRZM scenario:	MICherriesSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1109	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.05	fraction of application rate applied to pond

Application Date	Date	1-5	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	7	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1109	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

stored as MICHEGRD.out

Chemical: DPXE2Y45

PRZM environment: MICherriesSTD.txt	modified Tueday, 29 May 2007 at
12:56:56

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w14850.dvf	modified Wedday, 3 July 2002 at 09:05:40

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.1449	0.1404	0.1255	0.102	0.08956	0.04741

1962	0.4561	0.4406	0.3859	0.3001	0.2565	0.1268

1963	1.139	1.105	0.9766	0.7572	0.6412	0.2711

1964	0.3433	0.3322	0.2913	0.2471	0.2171	0.1612

1965	0.1739	0.169	0.1508	0.1332	0.1262	0.1071

1966	0.2367	0.2296	0.2029	0.1769	0.161	0.1095

1967	0.2875	0.2787	0.2463	0.2215	0.1992	0.1239

1968	0.1703	0.165	0.1457	0.1342	0.1208	0.07815

1969	0.7821	0.7579	0.699	0.5984	0.5072	0.2087

1970	0.2381	0.2319	0.2084	0.192	0.1721	0.1465

1971	0.1832	0.178	0.1585	0.1313	0.1237	0.1022

1972	0.3404	0.3294	0.3069	0.2488	0.2173	0.1278

1973	0.1699	0.1649	0.151	0.1324	0.1313	0.09379

1974	0.4152	0.403	0.3546	0.2874	0.2608	0.128

1975	0.3182	0.3092	0.2847	0.2327	0.2011	0.1274

1976	0.1706	0.1651	0.1464	0.1263	0.1107	0.09531

1977	0.2094	0.2027	0.1795	0.1596	0.1455	0.09916

1978	0.651	0.6291	0.5542	0.4389	0.3768	0.1839

1979	0.3494	0.3395	0.3076	0.2743	0.2532	0.1656

1980	0.2581	0.2504	0.2216	0.1755	0.166	0.1107

1981	0.5131	0.4964	0.4534	0.3848	0.3711	0.1836

1982	0.8733	0.8483	0.7433	0.5732	0.4911	0.2507

1983	0.4883	0.4747	0.4545	0.3886	0.3726	0.2286

1984	0.2015	0.1963	0.177	0.1668	0.157	0.1286

1985	0.7262	0.7002	0.6086	0.5243	0.4716	0.2113

1986	1.128	1.104	1.036	0.8254	0.7071	0.3587

1987	0.81	0.785	0.6966	0.5774	0.5092	0.2983

1988	0.2815	0.2738	0.266	0.2656	0.2651	0.1792

1989	0.7006	0.6781	0.5949	0.4894	0.4234	0.1947

1990	0.3838	0.3721	0.3504	0.2807	0.2461	0.1479

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	1.139	1.105	1.036	0.8254	0.7071	0.3587

0.0645161290322581	1.128	1.104	0.9766	0.7572	0.6412	0.2983

0.0967741935483871	0.8733	0.8483	0.7433	0.5984	0.5092	0.2711

0.129032258064516	0.81	0.785	0.699	0.5774	0.5072	0.2507

0.161290322580645	0.7821	0.7579	0.6966	0.5732	0.4911	0.2286

0.193548387096774	0.7262	0.7002	0.6086	0.5243	0.4716	0.2113

0.225806451612903	0.7006	0.6781	0.5949	0.4894	0.4234	0.2087

0.258064516129032	0.651	0.6291	0.5542	0.4389	0.3768	0.1947

0.290322580645161	0.5131	0.4964	0.4545	0.3886	0.3726	0.1839

0.32258064516129	0.4883	0.4747	0.4534	0.3848	0.3711	0.1836

0.354838709677419	0.4561	0.4406	0.3859	0.3001	0.2651	0.1792

0.387096774193548	0.4152	0.403	0.3546	0.2874	0.2608	0.1656

0.419354838709677	0.3838	0.3721	0.3504	0.2807	0.2565	0.1612

0.451612903225806	0.3494	0.3395	0.3076	0.2743	0.2532	0.1479

0.483870967741936	0.3433	0.3322	0.3069	0.2656	0.2461	0.1465

0.516129032258065	0.3404	0.3294	0.2913	0.2488	0.2173	0.1286

0.548387096774194	0.3182	0.3092	0.2847	0.2471	0.2171	0.128

0.580645161290323	0.2875	0.2787	0.266	0.2327	0.2011	0.1278

0.612903225806452	0.2815	0.2738	0.2463	0.2215	0.1992	0.1274

0.645161290322581	0.2581	0.2504	0.2216	0.192	0.1721	0.1268

0.67741935483871	0.2381	0.2319	0.2084	0.1769	0.166	0.1239

0.709677419354839	0.2367	0.2296	0.2029	0.1755	0.161	0.1107

0.741935483870968	0.2094	0.2027	0.1795	0.1668	0.157	0.1095

0.774193548387097	0.2015	0.1963	0.177	0.1596	0.1455	0.1071

0.806451612903226	0.1832	0.178	0.1585	0.1342	0.1313	0.1022

0.838709677419355	0.1739	0.169	0.151	0.1332	0.1262	0.09916

0.870967741935484	0.1706	0.1651	0.1508	0.1324	0.1237	0.09531

0.903225806451613	0.1703	0.165	0.1464	0.1313	0.1208	0.09379

0.935483870967742	0.1699	0.1649	0.1457	0.1263	0.1107	0.07815

0.967741935483871	0.1449	0.1404	0.1255	0.102	0.08956	0.04741

0.1	0.86697	0.84197	0.73887	0.5963	0.509	0.26906

					Average of yearly averages:	0.159860666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: MICHEGRD

Metfile:	w14850.dvf

PRZM scenario:	MICherriesSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1109	kg/ha

Application Efficiency:	APPEFF	0.99	fraction

Spray Drift	DRFT	0.01	fraction of application rate applied to pond

Application Date	Date	1-5	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	7	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1109	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

MS Cotton

stored as MSCOTAIR.out

Chemical: DPXE2Y45

PRZM environment: MScottonSTD.txt	modified Tueday, 29 May 2007 at
12:57:52

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w03940.dvf	modified Wedday, 3 July 2002 at 09:05:46

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	1.974	1.892	1.597	1.282	1.124	0.4016

1962	0.6839	0.6537	0.5466	0.4961	0.4313	0.1991

1963	2.242	2.155	1.842	1.43	1.222	0.4955

1964	0.8521	0.8184	0.6968	0.6228	0.5736	0.2732

1965	0.5559	0.5334	0.4527	0.3884	0.3425	0.1576

1966	3.755	3.682	3.281	2.392	1.951	0.679

1967	3.374	3.242	2.836	2.418	2.076	0.786

1968	2.232	2.143	2.01	1.541	1.273	0.4852

1969	0.7063	0.6781	0.5848	0.4717	0.4321	0.203

1970	1.003	0.963	0.8314	0.7401	0.6385	0.253

1971	3.051	2.926	2.503	1.85	1.523	0.5344

1972	1.992	1.941	1.761	1.389	1.174	0.4367

1973	2.094	2.009	1.771	1.397	1.16	0.4259

1974	1.434	1.376	1.166	0.8785	0.7808	0.3225

1975	2.872	2.777	2.608	2.037	1.701	0.6114

1976	4.097	3.942	3.604	2.908	2.451	0.8715

1977	1.092	1.056	0.9396	0.8405	0.7855	0.3857

1978	3.476	3.347	3.179	2.435	2	0.7046

1979	2.947	2.83	2.444	2.276	2.087	0.8059

1980	2.573	2.483	2.249	1.66	1.405	0.5311

1981	2.282	2.193	2.018	1.553	1.283	0.4709

1982	3.032	2.907	2.494	1.948	1.611	0.5997

1983	5.422	5.251	4.533	3.486	2.873	1.014

1984	1.596	1.548	1.407	1.22	1.06	0.4402

1985	0.5903	0.5693	0.5159	0.4673	0.434	0.2266

1986	2.536	2.439	2.162	1.654	1.369	0.4917

1987	1.525	1.467	1.296	1.144	1.034	0.409

1988	0.7223	0.695	0.6052	0.518	0.5002	0.2734

1989	3.771	3.636	3.175	2.655	2.314	0.8542

1990	3.008	2.896	2.568	1.99	1.641	0.608

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	5.422	5.251	4.533	3.486	2.873	1.014

0.0645161290322581	4.097	3.942	3.604	2.908	2.451	0.8715

0.0967741935483871	3.771	3.682	3.281	2.655	2.314	0.8542

0.129032258064516	3.755	3.636	3.179	2.435	2.087	0.8059

0.161290322580645	3.476	3.347	3.175	2.418	2.076	0.786

0.193548387096774	3.374	3.242	2.836	2.392	2	0.7046

0.225806451612903	3.051	2.926	2.608	2.276	1.951	0.679

0.258064516129032	3.032	2.907	2.568	2.037	1.701	0.6114

0.290322580645161	3.008	2.896	2.503	1.99	1.641	0.608

0.32258064516129	2.947	2.83	2.494	1.948	1.611	0.5997

0.354838709677419	2.872	2.777	2.444	1.85	1.523	0.5344

0.387096774193548	2.573	2.483	2.249	1.66	1.405	0.5311

0.419354838709677	2.536	2.439	2.162	1.654	1.369	0.4955

0.451612903225806	2.282	2.193	2.018	1.553	1.283	0.4917

0.483870967741936	2.242	2.155	2.01	1.541	1.273	0.4852

0.516129032258065	2.232	2.143	1.842	1.43	1.222	0.4709

0.548387096774194	2.094	2.009	1.771	1.397	1.174	0.4402

0.580645161290323	1.992	1.941	1.761	1.389	1.16	0.4367

0.612903225806452	1.974	1.892	1.597	1.282	1.124	0.4259

0.645161290322581	1.596	1.548	1.407	1.22	1.06	0.409

0.67741935483871	1.525	1.467	1.296	1.144	1.034	0.4016

0.709677419354839	1.434	1.376	1.166	0.8785	0.7855	0.3857

0.741935483870968	1.092	1.056	0.9396	0.8405	0.7808	0.3225

0.774193548387097	1.003	0.963	0.8314	0.7401	0.6385	0.2734

0.806451612903226	0.8521	0.8184	0.6968	0.6228	0.5736	0.2732

0.838709677419355	0.7223	0.695	0.6052	0.518	0.5002	0.253

0.870967741935484	0.7063	0.6781	0.5848	0.4961	0.434	0.2266

0.903225806451613	0.6839	0.6537	0.5466	0.4717	0.4321	0.203

0.935483870967742	0.5903	0.5693	0.5159	0.4673	0.4313	0.1991

0.967741935483871	0.5559	0.5334	0.4527	0.3884	0.3425	0.1576

0.1	3.7694	3.6774	3.2708	2.633	2.2913	0.84937

					Average of yearly averages:	0.498353333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: MSCOTAIR

Metfile:	w03940.dvf

PRZM scenario:	MScottonSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1109	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.05	fraction of application rate applied to pond

Application Date	Date	1-5	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	5	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1109	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

stored as MSCOTGRD.out

Chemical: DPXE2Y45

PRZM environment: MScottonSTD.txt	modified Tueday, 29 May 2007 at
12:57:52

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w03940.dvf	modified Wedday, 3 July 2002 at 09:05:46

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	1.634	1.566	1.323	1.087	0.9672	0.345

1962	0.3592	0.3466	0.3197	0.2576	0.2373	0.1339

1963	2.2	2.113	1.802	1.371	1.174	0.4407

1964	0.6208	0.5958	0.5266	0.485	0.4373	0.2082

1965	0.1979	0.1905	0.1722	0.1511	0.1367	0.08604

1966	3.575	3.511	3.128	2.279	1.858	0.6273

1967	3.187	3.062	2.686	2.256	1.942	0.7394

1968	1.927	1.851	1.762	1.36	1.125	0.4268

1969	0.3049	0.2933	0.2612	0.2389	0.24	0.1344

1970	0.6731	0.6555	0.5637	0.5025	0.4445	0.1851

1971	2.784	2.669	2.273	1.682	1.384	0.4784

1972	1.696	1.642	1.478	1.179	1.002	0.3773

1973	1.743	1.672	1.49	1.198	0.9964	0.3659

1974	1.242	1.191	1.007	0.7292	0.6122	0.2572

1975	2.598	2.503	2.348	1.854	1.553	0.5566

1976	3.885	3.738	3.439	2.767	2.339	0.8294

1977	1.007	0.9736	0.8662	0.7289	0.696	0.3256

1978	3.262	3.141	2.952	2.278	1.872	0.6575

1979	2.818	2.706	2.302	2.104	1.954	0.7615

1980	2.312	2.232	2.039	1.505	1.243	0.4777

1981	2.03	1.95	1.809	1.403	1.161	0.4131

1982	2.959	2.836	2.431	1.902	1.572	0.5478

1983	5.317	5.145	4.443	3.403	2.805	0.978

1984	1.247	1.2	1.112	1.009	0.891	0.3829

1985	0.4844	0.4663	0.4247	0.3678	0.3452	0.1587

1986	2.355	2.265	1.997	1.507	1.25	0.4336

1987	1.271	1.225	1.085	0.9272	0.8582	0.3467

1988	0.6819	0.6553	0.5685	0.4838	0.4526	0.2101

1989	3.572	3.445	3.011	2.49	2.182	0.8071

1990	2.733	2.631	2.344	1.833	1.513	0.555

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	5.317	5.145	4.443	3.403	2.805	0.978

0.0645161290322581	3.885	3.738	3.439	2.767	2.339	0.8294

0.0967741935483871	3.575	3.511	3.128	2.49	2.182	0.8071

0.129032258064516	3.572	3.445	3.011	2.279	1.954	0.7615

0.161290322580645	3.262	3.141	2.952	2.278	1.942	0.7394

0.193548387096774	3.187	3.062	2.686	2.256	1.872	0.6575

0.225806451612903	2.959	2.836	2.431	2.104	1.858	0.6273

0.258064516129032	2.818	2.706	2.348	1.902	1.572	0.5566

0.290322580645161	2.784	2.669	2.344	1.854	1.553	0.555

0.32258064516129	2.733	2.631	2.302	1.833	1.513	0.5478

0.354838709677419	2.598	2.503	2.273	1.682	1.384	0.4784

0.387096774193548	2.355	2.265	2.039	1.507	1.25	0.4777

0.419354838709677	2.312	2.232	1.997	1.505	1.243	0.4407

0.451612903225806	2.2	2.113	1.809	1.403	1.174	0.4336

0.483870967741936	2.03	1.95	1.802	1.371	1.161	0.4268

0.516129032258065	1.927	1.851	1.762	1.36	1.125	0.4131

0.548387096774194	1.743	1.672	1.49	1.198	1.002	0.3829

0.580645161290323	1.696	1.642	1.478	1.179	0.9964	0.3773

0.612903225806452	1.634	1.566	1.323	1.087	0.9672	0.3659

0.645161290322581	1.271	1.225	1.112	1.009	0.891	0.3467

0.67741935483871	1.247	1.2	1.085	0.9272	0.8582	0.345

0.709677419354839	1.242	1.191	1.007	0.7292	0.696	0.3256

0.741935483870968	1.007	0.9736	0.8662	0.7289	0.6122	0.2572

0.774193548387097	0.6819	0.6555	0.5685	0.5025	0.4526	0.2101

0.806451612903226	0.6731	0.6553	0.5637	0.485	0.4445	0.2082

0.838709677419355	0.6208	0.5958	0.5266	0.4838	0.4373	0.1851

0.870967741935484	0.4844	0.4663	0.4247	0.3678	0.3452	0.1587

0.903225806451613	0.3592	0.3466	0.3197	0.2576	0.24	0.1344

0.935483870967742	0.3049	0.2933	0.2612	0.2389	0.2373	0.1339

0.967741935483871	0.1979	0.1905	0.1722	0.1511	0.1367	0.08604

0.1	3.5747	3.5044	3.1163	2.4689	2.1592	0.80254

					Average of yearly averages:	0.441564666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: MSCOTGRD

Metfile:	w03940.dvf

PRZM scenario:	MScottonSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1109	kg/ha

Application Efficiency:	APPEFF	0.99	fraction

Spray Drift	DRFT	0.01	fraction of application rate applied to pond

Application Date	Date	1-5	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	5	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1109	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

NY Grape

stored as CACOTAIR.out

Chemical: DPXE2Y45

PRZM environment: NYGrapesSTD.txt	modified Tueday, 29 May 2007 at
12:59:44

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w14860.dvf	modified Wedday, 3 July 2002 at 09:06:14

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.6227	0.601	0.522	0.4139	0.3586	0.1378

1962	1.601	1.553	1.413	1.127	1.042	0.467

1963	0.6865	0.6628	0.5766	0.475	0.4419	0.3278

1964	0.965	0.9339	0.8196	0.6472	0.583	0.3334

1965	0.7813	0.755	0.659	0.5772	0.5281	0.3087

1966	0.9513	0.9191	0.8551	0.6759	0.6125	0.3121

1967	1.391	1.347	1.198	0.9476	0.8383	0.4086

1968	0.6522	0.6315	0.5555	0.4478	0.3968	0.2587

1969	0.6483	0.628	0.5592	0.4722	0.4114	0.2128

1970	1.017	0.985	0.9071	0.7132	0.6446	0.3366

1971	0.7442	0.7217	0.6374	0.5544	0.5379	0.3441

1972	1.237	1.204	1.108	0.9193	0.8092	0.3947

1973	1.366	1.326	1.184	0.9757	0.8576	0.4227

1974	1.185	1.152	1.006	0.8182	0.7407	0.4068

1975	0.9142	0.8853	0.7819	0.6567	0.6344	0.4152

1976	0.7971	0.779	0.6907	0.6084	0.5495	0.3153

1977	0.8011	0.7746	0.6806	0.6506	0.6132	0.3332

1978	0.6798	0.659	0.6045	0.5284	0.4883	0.341

1979	0.8796	0.8525	0.7577	0.7281	0.6956	0.4361

1980	1.261	1.227	1.101	1.048	1.033	0.5739

1981	0.7703	0.7468	0.6927	0.6054	0.5599	0.3845

1982	1.231	1.197	1.07	0.8891	0.7937	0.386

1983	1.055	1.02	0.9309	0.8751	0.7917	0.4202

1984	1.225	1.188	1.06	0.839	0.7409	0.4251

1985	1.121	1.087	0.9643	0.8622	0.7647	0.4021

1986	1.826	1.774	1.593	1.272	1.102	0.5831

1987	0.8003	0.7751	0.707	0.6372	0.6114	0.3996

1988	0.6041	0.5815	0.4996	0.4028	0.3979	0.2646

1989	1.028	1.002	0.8867	0.7151	0.634	0.3272

1990	0.6992	0.6816	0.6521	0.5471	0.4814	0.2981

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	1.826	1.774	1.593	1.272	1.102	0.5831

0.0645161290322581	1.601	1.553	1.413	1.127	1.042	0.5739

0.0967741935483871	1.391	1.347	1.198	1.048	1.033	0.467

0.129032258064516	1.366	1.326	1.184	0.9757	0.8576	0.4361

0.161290322580645	1.261	1.227	1.108	0.9476	0.8383	0.4251

0.193548387096774	1.237	1.204	1.101	0.9193	0.8092	0.4227

0.225806451612903	1.231	1.197	1.07	0.8891	0.7937	0.4202

0.258064516129032	1.225	1.188	1.06	0.8751	0.7917	0.4152

0.290322580645161	1.185	1.152	1.006	0.8622	0.7647	0.4086

0.32258064516129	1.121	1.087	0.9643	0.839	0.7409	0.4068

0.354838709677419	1.055	1.02	0.9309	0.8182	0.7407	0.4021

0.387096774193548	1.028	1.002	0.9071	0.7281	0.6956	0.3996

0.419354838709677	1.017	0.985	0.8867	0.7151	0.6446	0.3947

0.451612903225806	0.965	0.9339	0.8551	0.7132	0.6344	0.386

0.483870967741936	0.9513	0.9191	0.8196	0.6759	0.634	0.3845

0.516129032258065	0.9142	0.8853	0.7819	0.6567	0.6132	0.3441

0.548387096774194	0.8796	0.8525	0.7577	0.6506	0.6125	0.341

0.580645161290323	0.8011	0.779	0.707	0.6472	0.6114	0.3366

0.612903225806452	0.8003	0.7751	0.6927	0.6372	0.583	0.3334

0.645161290322581	0.7971	0.7746	0.6907	0.6084	0.5599	0.3332

0.67741935483871	0.7813	0.755	0.6806	0.6054	0.5495	0.3278

0.709677419354839	0.7703	0.7468	0.659	0.5772	0.5379	0.3272

0.741935483870968	0.7442	0.7217	0.6521	0.5544	0.5281	0.3153

0.774193548387097	0.6992	0.6816	0.6374	0.5471	0.4883	0.3121

0.806451612903226	0.6865	0.6628	0.6045	0.5284	0.4814	0.3087

0.838709677419355	0.6798	0.659	0.5766	0.475	0.4419	0.2981

0.870967741935484	0.6522	0.6315	0.5592	0.4722	0.4114	0.2646

0.903225806451613	0.6483	0.628	0.5555	0.4478	0.3979	0.2587

0.935483870967742	0.6227	0.601	0.522	0.4139	0.3968	0.2128

0.967741935483871	0.6041	0.5815	0.4996	0.4028	0.3586	0.1378

0.1	1.3885	1.3449	1.1966	1.04077	1.01546	0.46391

					Average of yearly averages:	0.3659

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CACOTAIR

Metfile:	w14860.dvf

PRZM scenario:	NYGrapesSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1109	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.05	fraction of application rate applied to pond

Application Date	Date	1-6	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	7	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1109	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

stored as CACOTGRD.out

Chemical: DPXE2Y45

PRZM environment: NYGrapesSTD.txt	modified Tueday, 29 May 2007 at
12:59:44

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w14860.dvf	modified Wedday, 3 July 2002 at 09:06:14

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.2116	0.2052	0.1819	0.1552	0.1404	0.06229

1962	1.252	1.215	1.107	0.9013	0.8587	0.3821

1963	0.3809	0.3809	0.3808	0.379	0.3624	0.2357

1964	0.8258	0.798	0.6966	0.5351	0.463	0.242

1965	0.5476	0.5289	0.4604	0.3654	0.322	0.2148

1966	0.6023	0.5836	0.5247	0.432	0.4124	0.2244

1967	1.196	1.158	1.03	0.816	0.7059	0.3256

1968	0.2714	0.2713	0.2703	0.2661	0.2557	0.1628

1969	0.226	0.2209	0.1976	0.1817	0.1648	0.1035

1970	0.7995	0.7732	0.7189	0.5652	0.5085	0.2292

1971	0.5538	0.5365	0.4723	0.3845	0.3437	0.2397

1972	0.9302	0.9037	0.835	0.6958	0.6025	0.2942

1973	0.9965	0.97	0.8706	0.7173	0.641	0.3275

1974	0.9102	0.886	0.7753	0.6127	0.5532	0.31

1975	0.6902	0.67	0.6174	0.5014	0.4652	0.3159

1976	0.5196	0.5097	0.4539	0.3837	0.3386	0.2193

1977	0.5921	0.5838	0.5487	0.4894	0.4522	0.2351

1978	0.5146	0.4981	0.4605	0.4139	0.3852	0.2377

1979	0.8021	0.7765	0.6855	0.6144	0.5992	0.3416

1980	1.126	1.096	0.9816	0.8966	0.831	0.4865

1981	0.4403	0.428	0.4105	0.4083	0.3899	0.2872

1982	0.8759	0.8539	0.7697	0.6385	0.5766	0.2893

1983	0.8861	0.8583	0.808	0.7118	0.6563	0.3349

1984	0.8871	0.8623	0.7791	0.624	0.5614	0.3368

1985	0.7437	0.7233	0.6701	0.6263	0.5647	0.3138

1986	1.471	1.432	1.29	1.045	0.9048	0.4954

1987	0.5436	0.5276	0.4709	0.4313	0.4072	0.3116

1988	0.3362	0.325	0.2944	0.2721	0.2579	0.1751

1989	0.699	0.6842	0.6095	0.4778	0.4307	0.2366

1990	0.6079	0.5908	0.5591	0.4688	0.4051	0.2067

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	1.471	1.432	1.29	1.045	0.9048	0.4954

0.0645161290322581	1.252	1.215	1.107	0.9013	0.8587	0.4865

0.0967741935483871	1.196	1.158	1.03	0.8966	0.831	0.3821

0.129032258064516	1.126	1.096	0.9816	0.816	0.7059	0.3416

0.161290322580645	0.9965	0.97	0.8706	0.7173	0.6563	0.3368

0.193548387096774	0.9302	0.9037	0.835	0.7118	0.641	0.3349

0.225806451612903	0.9102	0.886	0.808	0.6958	0.6025	0.3275

0.258064516129032	0.8871	0.8623	0.7791	0.6385	0.5992	0.3256

0.290322580645161	0.8861	0.8583	0.7753	0.6263	0.5766	0.3159

0.32258064516129	0.8759	0.8539	0.7697	0.624	0.5647	0.3138

0.354838709677419	0.8258	0.798	0.7189	0.6144	0.5614	0.3116

0.387096774193548	0.8021	0.7765	0.6966	0.6127	0.5532	0.31

0.419354838709677	0.7995	0.7732	0.6855	0.5652	0.5085	0.2942

0.451612903225806	0.7437	0.7233	0.6701	0.5351	0.4652	0.2893

0.483870967741936	0.699	0.6842	0.6174	0.5014	0.463	0.2872

0.516129032258065	0.6902	0.67	0.6095	0.4894	0.4522	0.242

0.548387096774194	0.6079	0.5908	0.5591	0.4778	0.4307	0.2397

0.580645161290323	0.6023	0.5838	0.5487	0.4688	0.4124	0.2377

0.612903225806452	0.5921	0.5836	0.5247	0.432	0.4072	0.2366

0.645161290322581	0.5538	0.5365	0.4723	0.4313	0.4051	0.2357

0.67741935483871	0.5476	0.5289	0.4709	0.4139	0.3899	0.2351

0.709677419354839	0.5436	0.5276	0.4605	0.4083	0.3852	0.2292

0.741935483870968	0.5196	0.5097	0.4604	0.3845	0.3624	0.2244

0.774193548387097	0.5146	0.4981	0.4539	0.3837	0.3437	0.2193

0.806451612903226	0.4403	0.428	0.4105	0.379	0.3386	0.2148

0.838709677419355	0.3809	0.3809	0.3808	0.3654	0.322	0.2067

0.870967741935484	0.3362	0.325	0.2944	0.2721	0.2579	0.1751

0.903225806451613	0.2714	0.2713	0.2703	0.2661	0.2557	0.1628

0.935483870967742	0.226	0.2209	0.1976	0.1817	0.1648	0.1035

0.967741935483871	0.2116	0.2052	0.1819	0.1552	0.1404	0.06229

0.1	1.189	1.1518	1.02516	0.88854	0.81849	0.37805

					Average of yearly averages:	0.272576333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CACOTGRD

Metfile:	w14860.dvf

PRZM scenario:	NYGrapesSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1109	kg/ha

Application Efficiency:	APPEFF	0.99	fraction

Spray Drift	DRFT	0.01	fraction of application rate applied to pond

Application Date	Date	1-6	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	7	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1109	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

OR Apple

stored as ORAPPAIR.out

Chemical: DPXE2Y45

PRZM environment: ORappleSTD.txt	modified Tueday, 29 May 2007 at
13:00:08

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w24232.dvf	modified Wedday, 3 July 2002 at 09:06:10

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.5132	0.4972	0.4627	0.4047	0.353	0.1386

1962	0.6215	0.6032	0.5428	0.4781	0.42	0.1917

1963	1.02	0.9866	0.8716	0.6926	0.6318	0.2926

1964	0.5819	0.5645	0.5003	0.4024	0.3528	0.1865

1965	0.5918	0.581	0.5494	0.446	0.3906	0.2005

1966	0.5788	0.5601	0.4917	0.3907	0.3381	0.1861

1967	0.605	0.5871	0.5211	0.4213	0.3665	0.19

1968	0.5624	0.5447	0.4798	0.39	0.3533	0.1867

1969	0.5621	0.5456	0.4852	0.3856	0.3416	0.1958

1970	0.5729	0.5563	0.4948	0.3944	0.3417	0.1629

1971	1.021	0.9898	0.8743	0.6911	0.5961	0.2761

1972	0.6404	0.6238	0.5554	0.4741	0.4248	0.2025

1973	0.5686	0.5504	0.4839	0.3842	0.3336	0.1617

1974	0.556	0.5397	0.4794	0.3838	0.3346	0.1889

1975	0.6318	0.6137	0.5475	0.4673	0.4126	0.2204

1976	0.5588	0.5418	0.4792	0.3804	0.3304	0.1447

1977	0.5347	0.517	0.4521	0.3719	0.3309	0.1457

1978	0.6196	0.6011	0.5366	0.4837	0.4374	0.1977

1979	0.5633	0.5469	0.4862	0.4223	0.3731	0.1845

1980	0.7261	0.7028	0.6335	0.5097	0.4528	0.2097

1981	0.7922	0.768	0.6789	0.5424	0.4993	0.2495

1982	0.7236	0.7029	0.6287	0.491	0.4274	0.1934

1983	0.5745	0.5558	0.4873	0.3973	0.3496	0.1622

1984	0.7213	0.6999	0.6275	0.5595	0.5029	0.2192

1985	0.5535	0.5361	0.4719	0.3842	0.3799	0.1973

1986	0.5747	0.5574	0.495	0.4096	0.3595	0.1687

1987	0.6032	0.5839	0.5316	0.4222	0.3667	0.1951

1988	0.6195	0.6018	0.5672	0.4673	0.4147	0.2033

1989	0.5533	0.5357	0.4708	0.374	0.3246	0.1738

1990	0.6123	0.5941	0.5314	0.4379	0.3872	0.2107

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	1.021	0.9898	0.8743	0.6926	0.6318	0.2926

0.0645161290322581	1.02	0.9866	0.8716	0.6911	0.5961	0.2761

0.0967741935483871	0.7922	0.768	0.6789	0.5595	0.5029	0.2495

0.129032258064516	0.7261	0.7029	0.6335	0.5424	0.4993	0.2204

0.161290322580645	0.7236	0.7028	0.6287	0.5097	0.4528	0.2192

0.193548387096774	0.7213	0.6999	0.6275	0.491	0.4374	0.2107

0.225806451612903	0.6404	0.6238	0.5672	0.4837	0.4274	0.2097

0.258064516129032	0.6318	0.6137	0.5554	0.4781	0.4248	0.2033

0.290322580645161	0.6215	0.6032	0.5494	0.4741	0.42	0.2025

0.32258064516129	0.6196	0.6018	0.5475	0.4673	0.4147	0.2005

0.354838709677419	0.6195	0.6011	0.5428	0.4673	0.4126	0.1977

0.387096774193548	0.6123	0.5941	0.5366	0.446	0.3906	0.1973

0.419354838709677	0.605	0.5871	0.5316	0.4379	0.3872	0.1958

0.451612903225806	0.6032	0.5839	0.5314	0.4223	0.3799	0.1951

0.483870967741936	0.5918	0.581	0.5211	0.4222	0.3731	0.1934

0.516129032258065	0.5819	0.5645	0.5003	0.4213	0.3667	0.1917

0.548387096774194	0.5788	0.5601	0.495	0.4096	0.3665	0.19

0.580645161290323	0.5747	0.5574	0.4948	0.4047	0.3595	0.1889

0.612903225806452	0.5745	0.5563	0.4917	0.4024	0.3533	0.1867

0.645161290322581	0.5729	0.5558	0.4873	0.3973	0.353	0.1865

0.67741935483871	0.5686	0.5504	0.4862	0.3944	0.3528	0.1861

0.709677419354839	0.5633	0.5469	0.4852	0.3907	0.3496	0.1845

0.741935483870968	0.5624	0.5456	0.4839	0.39	0.3417	0.1738

0.774193548387097	0.5621	0.5447	0.4798	0.3856	0.3416	0.1687

0.806451612903226	0.5588	0.5418	0.4794	0.3842	0.3381	0.1629

0.838709677419355	0.556	0.5397	0.4792	0.3842	0.3346	0.1622

0.870967741935484	0.5535	0.5361	0.4719	0.3838	0.3336	0.1617

0.903225806451613	0.5533	0.5357	0.4708	0.3804	0.3309	0.1457

0.935483870967742	0.5347	0.517	0.4627	0.374	0.3304	0.1447

0.967741935483871	0.5132	0.4972	0.4521	0.3719	0.3246	0.1386

0.1	0.78559	0.76149	0.67436	0.55779	0.50254	0.24659

					Average of yearly averages:	0.19455

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: ORAPPAIR

Metfile:	w24232.dvf

PRZM scenario:	ORappleSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1109	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.05	fraction of application rate applied to pond

Application Date	Date	1-4	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	10	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1109	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

stored as ORAPPGRD.out

Chemical: DPXE2Y45

PRZM environment: ORappleSTD.txt	modified Tueday, 29 May 2007 at
13:00:08

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w24232.dvf	modified Wedday, 3 July 2002 at 09:06:10

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.1958	0.1899	0.1681	0.1333	0.1174	0.04997

1962	0.2981	0.2891	0.2604	0.2071	0.1762	0.09175

1963	0.7417	0.7168	0.628	0.4889	0.4167	0.1922

1964	0.2058	0.2016	0.19	0.1584	0.1143	0.08408

1965	0.2241	0.2186	0.1974	0.1623	0.1435	0.1026

1966	0.2874	0.2817	0.2604	0.2042	0.1441	0.09132

1967	0.1903	0.1865	0.1719	0.1448	0.1286	0.09588

1968	0.165	0.1619	0.1439	0.1271	0.1173	0.08935

1969	0.1944	0.1887	0.1705	0.1524	0.1409	0.0961

1970	0.1466	0.1428	0.1288	0.107	0.09362	0.06485

1971	0.614	0.5952	0.5358	0.4192	0.3624	0.1793

1972	0.2641	0.2577	0.2278	0.1943	0.1816	0.1058

1973	0.1457	0.1415	0.1264	0.1044	0.09149	0.06517

1974	0.4132	0.4043	0.3692	0.3065	0.2105	0.08935

1975	0.2566	0.2515	0.2318	0.1967	0.1751	0.1241

1976	0.1336	0.1299	0.1161	0.09507	0.08319	0.0452

1977	0.1194	0.1162	0.1041	0.09271	0.08473	0.04667

1978	0.3652	0.3535	0.3115	0.2412	0.2032	0.09736

1979	0.1963	0.1911	0.1701	0.1383	0.124	0.08516

1980	0.3094	0.2997	0.2813	0.2333	0.2133	0.1123

1981	0.3766	0.3653	0.3238	0.2647	0.2635	0.1524

1982	0.3287	0.3185	0.2834	0.2214	0.19	0.09808

1983	0.1516	0.147	0.1299	0.1188	0.1075	0.06325

1984	0.3708	0.3597	0.3185	0.2781	0.2638	0.12

1985	0.3097	0.2989	0.2623	0.1966	0.1634	0.1022

1986	0.153	0.149	0.1344	0.1253	0.113	0.07091

1987	0.2705	0.2662	0.2499	0.1603	0.1279	0.1023

1988	0.2379	0.2319	0.2112	0.1826	0.1664	0.1064

1989	0.2974	0.2895	0.2603	0.2081	0.1556	0.07564

1990	0.2103	0.2058	0.1962	0.1659	0.1468	0.111

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	0.7417	0.7168	0.628	0.4889	0.4167	0.1922

0.0645161290322581	0.614	0.5952	0.5358	0.4192	0.3624	0.1793

0.0967741935483871	0.4132	0.4043	0.3692	0.3065	0.2638	0.1524

0.129032258064516	0.3766	0.3653	0.3238	0.2781	0.2635	0.1241

0.161290322580645	0.3708	0.3597	0.3185	0.2647	0.2133	0.12

0.193548387096774	0.3652	0.3535	0.3115	0.2412	0.2105	0.1123

0.225806451612903	0.3287	0.3185	0.2834	0.2333	0.2032	0.111

0.258064516129032	0.3097	0.2997	0.2813	0.2214	0.19	0.1064

0.290322580645161	0.3094	0.2989	0.2623	0.2081	0.1816	0.1058

0.32258064516129	0.2981	0.2895	0.2604	0.2071	0.1762	0.1026

0.354838709677419	0.2974	0.2891	0.2604	0.2042	0.1751	0.1023

0.387096774193548	0.2874	0.2817	0.2603	0.1967	0.1664	0.1022

0.419354838709677	0.2705	0.2662	0.2499	0.1966	0.1634	0.09808

0.451612903225806	0.2641	0.2577	0.2318	0.1943	0.1556	0.09736

0.483870967741936	0.2566	0.2515	0.2278	0.1826	0.1468	0.0961

0.516129032258065	0.2379	0.2319	0.2112	0.1659	0.1441	0.09588

0.548387096774194	0.2241	0.2186	0.1974	0.1623	0.1435	0.09175

0.580645161290323	0.2103	0.2058	0.1962	0.1603	0.1409	0.09132

0.612903225806452	0.2058	0.2016	0.19	0.1584	0.1286	0.08935

0.645161290322581	0.1963	0.1911	0.1719	0.1524	0.1279	0.08935

0.67741935483871	0.1958	0.1899	0.1705	0.1448	0.124	0.08516

0.709677419354839	0.1944	0.1887	0.1701	0.1383	0.1174	0.08408

0.741935483870968	0.1903	0.1865	0.1681	0.1333	0.1173	0.07564

0.774193548387097	0.165	0.1619	0.1439	0.1271	0.1143	0.07091

0.806451612903226	0.153	0.149	0.1344	0.1253	0.113	0.06517

0.838709677419355	0.1516	0.147	0.1299	0.1188	0.1075	0.06485

0.870967741935484	0.1466	0.1428	0.1288	0.107	0.09362	0.06325

0.903225806451613	0.1457	0.1415	0.1264	0.1044	0.09149	0.04997

0.935483870967742	0.1336	0.1299	0.1161	0.09507	0.08473	0.04667

0.967741935483871	0.1194	0.1162	0.1041	0.09271	0.08319	0.0452

0.1	0.40954	0.4004	0.36466	0.30366	0.26377	0.14957

					Average of yearly averages:	0.097023

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: ORAPPGRD

Metfile:	w24232.dvf

PRZM scenario:	ORappleSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1109	kg/ha

Application Efficiency:	APPEFF	0.99	fraction

Spray Drift	DRFT	0.01	fraction of application rate applied to pond

Application Date	Date	1-4	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	10	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1109	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

PA Apple

stored as PAPPAIR.out

Chemical: DPXE2Y45

PRZM environment: PAappleSTD.txt	modified Tueday, 29 May 2007 at
13:01:58

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w14751.dvf	modified Wedday, 3 July 2002 at 09:06:14

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.5156	0.4987	0.4348	0.3375	0.2992	0.1616

1962	0.5648	0.546	0.4811	0.3868	0.3526	0.1682

1963	0.5472	0.5276	0.4556	0.3622	0.3158	0.1411

1964	0.6947	0.6698	0.5816	0.4784	0.4227	0.1836

1965	0.5501	0.5324	0.4729	0.3769	0.3326	0.147

1966	0.7679	0.7417	0.6486	0.4962	0.421	0.2388

1967	0.7069	0.6845	0.619	0.5151	0.4586	0.2369

1968	1.233	1.204	1.054	0.8052	0.7347	0.3127

1969	0.688	0.6662	0.6033	0.4594	0.3863	0.2459

1970	0.5955	0.5758	0.5112	0.409	0.382	0.1931

1971	0.6312	0.6108	0.5381	0.4678	0.407	0.1741

1972	0.7282	0.7067	0.628	0.5435	0.5398	0.2454

1973	0.7558	0.7339	0.6462	0.6022	0.5366	0.2329

1974	0.9022	0.8716	0.7651	0.6056	0.5469	0.2409

1975	1.024	0.9905	0.8854	0.7366	0.6485	0.2689

1976	0.6597	0.6403	0.5938	0.5187	0.4618	0.207

1977	0.6427	0.6197	0.5352	0.4128	0.3677	0.1705

1978	0.843	0.8162	0.7315	0.5873	0.5253	0.2273

1979	0.637	0.6191	0.5524	0.4827	0.4469	0.2078

1980	0.9083	0.8776	0.8108	0.6902	0.5965	0.2423

1981	0.5602	0.5418	0.4717	0.3706	0.3377	0.1636

1982	1.246	1.208	1.095	0.8622	0.7223	0.3134

1983	0.9794	0.9482	0.8373	0.7841	0.6788	0.2794

1984	0.9339	0.9049	0.7971	0.6402	0.5909	0.2695

1985	1.307	1.263	1.157	0.9976	0.8574	0.3593

1986	1.064	1.03	0.9144	0.7923	0.6822	0.3248

1987	0.5819	0.5639	0.5244	0.4798	0.4472	0.2131

1988	0.5832	0.5644	0.5448	0.4747	0.4121	0.1769

1989	1.649	1.598	1.502	1.179	1.005	0.3943

1990	1.091	1.058	0.9257	0.789	0.7045	0.3207

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	1.649	1.598	1.502	1.179	1.005	0.3943

0.0645161290322581	1.307	1.263	1.157	0.9976	0.8574	0.3593

0.0967741935483871	1.246	1.208	1.095	0.8622	0.7347	0.3248

0.129032258064516	1.233	1.204	1.054	0.8052	0.7223	0.3207

0.161290322580645	1.091	1.058	0.9257	0.7923	0.7045	0.3134

0.193548387096774	1.064	1.03	0.9144	0.789	0.6822	0.3127

0.225806451612903	1.024	0.9905	0.8854	0.7841	0.6788	0.2794

0.258064516129032	0.9794	0.9482	0.8373	0.7366	0.6485	0.2695

0.290322580645161	0.9339	0.9049	0.8108	0.6902	0.5965	0.2689

0.32258064516129	0.9083	0.8776	0.7971	0.6402	0.5909	0.2459

0.354838709677419	0.9022	0.8716	0.7651	0.6056	0.5469	0.2454

0.387096774193548	0.843	0.8162	0.7315	0.6022	0.5398	0.2423

0.419354838709677	0.7679	0.7417	0.6486	0.5873	0.5366	0.2409

0.451612903225806	0.7558	0.7339	0.6462	0.5435	0.5253	0.2388

0.483870967741936	0.7282	0.7067	0.628	0.5187	0.4618	0.2369

0.516129032258065	0.7069	0.6845	0.619	0.5151	0.4586	0.2329

0.548387096774194	0.6947	0.6698	0.6033	0.4962	0.4472	0.2273

0.580645161290323	0.688	0.6662	0.5938	0.4827	0.4469	0.2131

0.612903225806452	0.6597	0.6403	0.5816	0.4798	0.4227	0.2078

0.645161290322581	0.6427	0.6197	0.5524	0.4784	0.421	0.207

0.67741935483871	0.637	0.6191	0.5448	0.4747	0.4121	0.1931

0.709677419354839	0.6312	0.6108	0.5381	0.4678	0.407	0.1836

0.741935483870968	0.5955	0.5758	0.5352	0.4594	0.3863	0.1769

0.774193548387097	0.5832	0.5644	0.5244	0.4128	0.382	0.1741

0.806451612903226	0.5819	0.5639	0.5112	0.409	0.3677	0.1705

0.838709677419355	0.5648	0.546	0.4811	0.3868	0.3526	0.1682

0.870967741935484	0.5602	0.5418	0.4729	0.3769	0.3377	0.1636

0.903225806451613	0.5501	0.5324	0.4717	0.3706	0.3326	0.1616

0.935483870967742	0.5472	0.5276	0.4556	0.3622	0.3158	0.147

0.967741935483871	0.5156	0.4987	0.4348	0.3375	0.2992	0.1411

0.1	1.2447	1.2076	1.0909	0.8565	0.73346	0.32439

					Average of yearly averages:	0.235366666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: PAPPAIR

Metfile:	w14751.dvf

PRZM scenario:	PAappleSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1109	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.05	fraction of application rate applied to pond

Application Date	Date	16-4	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	10	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1109	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

stored as PAPPGRD.out

Chemical: DPXE2Y45

PRZM environment: PAappleSTD.txt	modified Tueday, 29 May 2007 at
13:01:58

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w14751.dvf	modified Wedday, 3 July 2002 at 09:06:14

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.3645	0.3511	0.3128	0.2425	0.2028	0.08188

1962	0.1838	0.1777	0.1553	0.1227	0.1216	0.07592

1963	0.1217	0.1176	0.1022	0.08989	0.08388	0.04855

1964	0.3016	0.2906	0.2483	0.2263	0.2116	0.09417

1965	0.1306	0.1261	0.117	0.1072	0.1006	0.0568

1966	0.7373	0.7111	0.6185	0.4686	0.3952	0.1516

1967	0.3693	0.3581	0.3166	0.2527	0.2343	0.1487

1968	1.016	0.9928	0.8669	0.652	0.5436	0.2262

1969	0.6026	0.5823	0.5225	0.3929	0.327	0.1589

1970	0.2054	0.2008	0.1894	0.1624	0.1542	0.102

1971	0.3285	0.3177	0.2774	0.2157	0.1843	0.08483

1972	0.5723	0.5544	0.4879	0.3762	0.3405	0.1566

1973	0.5121	0.4966	0.435	0.3417	0.3126	0.1409

1974	0.6063	0.5851	0.5136	0.4113	0.3599	0.1547

1975	0.6823	0.6594	0.5959	0.4933	0.4362	0.1825

1976	0.4029	0.3892	0.3531	0.3022	0.2597	0.1188

1977	0.222	0.2143	0.1871	0.1439	0.1404	0.07652

1978	0.548	0.5295	0.4746	0.3725	0.3197	0.1325

1979	0.3781	0.3657	0.3261	0.2737	0.2418	0.1133

1980	0.6574	0.6345	0.5608	0.4502	0.3916	0.1572

1981	0.1505	0.1457	0.131	0.1159	0.1074	0.07102

1982	1.056	1.023	0.9187	0.7229	0.6033	0.2271

1983	0.7299	0.7061	0.6169	0.5308	0.4686	0.1958

1984	0.7029	0.68	0.5985	0.4832	0.4087	0.1785

1985	1.051	1.015	0.901	0.782	0.6725	0.2731

1986	0.6964	0.6736	0.6225	0.5325	0.4616	0.2357

1987	0.3545	0.3424	0.2974	0.2527	0.23	0.1234

1988	0.3017	0.2918	0.262	0.2158	0.1864	0.08728

1989	1.347	1.302	1.243	0.9778	0.8256	0.3109

1990	0.8701	0.8426	0.7342	0.5865	0.5211	0.2326

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	1.347	1.302	1.243	0.9778	0.8256	0.3109

0.0645161290322581	1.056	1.023	0.9187	0.782	0.6725	0.2731

0.0967741935483871	1.051	1.015	0.901	0.7229	0.6033	0.2357

0.129032258064516	1.016	0.9928	0.8669	0.652	0.5436	0.2326

0.161290322580645	0.8701	0.8426	0.7342	0.5865	0.5211	0.2271

0.193548387096774	0.7373	0.7111	0.6225	0.5325	0.4686	0.2262

0.225806451612903	0.7299	0.7061	0.6185	0.5308	0.4616	0.1958

0.258064516129032	0.7029	0.68	0.6169	0.4933	0.4362	0.1825

0.290322580645161	0.6964	0.6736	0.5985	0.4832	0.4087	0.1785

0.32258064516129	0.6823	0.6594	0.5959	0.4686	0.3952	0.1589

0.354838709677419	0.6574	0.6345	0.5608	0.4502	0.3916	0.1572

0.387096774193548	0.6063	0.5851	0.5225	0.4113	0.3599	0.1566

0.419354838709677	0.6026	0.5823	0.5136	0.3929	0.3405	0.1547

0.451612903225806	0.5723	0.5544	0.4879	0.3762	0.327	0.1516

0.483870967741936	0.548	0.5295	0.4746	0.3725	0.3197	0.1487

0.516129032258065	0.5121	0.4966	0.435	0.3417	0.3126	0.1409

0.548387096774194	0.4029	0.3892	0.3531	0.3022	0.2597	0.1325

0.580645161290323	0.3781	0.3657	0.3261	0.2737	0.2418	0.1234

0.612903225806452	0.3693	0.3581	0.3166	0.2527	0.2343	0.1188

0.645161290322581	0.3645	0.3511	0.3128	0.2527	0.23	0.1133

0.67741935483871	0.3545	0.3424	0.2974	0.2425	0.2116	0.102

0.709677419354839	0.3285	0.3177	0.2774	0.2263	0.2028	0.09417

0.741935483870968	0.3017	0.2918	0.262	0.2158	0.1864	0.08728

0.774193548387097	0.3016	0.2906	0.2483	0.2157	0.1843	0.08483

0.806451612903226	0.222	0.2143	0.1894	0.1624	0.1542	0.08188

0.838709677419355	0.2054	0.2008	0.1871	0.1439	0.1404	0.07652

0.870967741935484	0.1838	0.1777	0.1553	0.1227	0.1216	0.07592

0.903225806451613	0.1505	0.1457	0.131	0.1159	0.1074	0.07102

0.935483870967742	0.1306	0.1261	0.117	0.1072	0.1006	0.0568

0.967741935483871	0.1217	0.1176	0.1022	0.08989	0.08388	0.04855

0.1	1.0475	1.01278	0.89759	0.71581	0.59733	0.23539

					Average of yearly averages:	0.146599

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: PAPPGRD

Metfile:	w14751.dvf

PRZM scenario:	PAappleSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1109	kg/ha

Application Efficiency:	APPEFF	0.99	fraction

Spray Drift	DRFT	0.01	fraction of application rate applied to pond

Application Date	Date	16-4	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	10	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1109	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

PA Tomato

stored as PATOMAIR.out

Chemical: DPXE2Y45

PRZM environment: PAtomatoSTD.txt	modified Tueday, 29 May 2007 at
13:01:58

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w14751.dvf	modified Wedday, 3 July 2002 at 09:06:14

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.5779	0.5588	0.4892	0.3789	0.3258	0.1736

1962	0.5862	0.5665	0.5314	0.4455	0.4094	0.1944

1963	0.5752	0.5546	0.481	0.381	0.3322	0.1527

1964	0.7409	0.7146	0.6125	0.5322	0.483	0.2098

1965	0.5739	0.5554	0.5014	0.4201	0.3771	0.1721

1966	0.6966	0.6741	0.605	0.487	0.4128	0.2491

1967	0.7598	0.7356	0.6531	0.5664	0.4981	0.2456

1968	1.367	1.338	1.178	1.012	0.9216	0.3787

1969	0.7754	0.7508	0.6786	0.5174	0.4352	0.2779

1970	0.6433	0.6219	0.5642	0.4579	0.4233	0.2129

1971	0.6625	0.6422	0.5756	0.5047	0.4417	0.1906

1972	0.7365	0.712	0.6574	0.5801	0.575	0.2573

1973	0.8698	0.8417	0.7504	0.6937	0.6205	0.2613

1974	1.07	1.034	0.9218	0.7363	0.6492	0.2896

1975	1.325	1.281	1.163	0.9723	0.8423	0.3407

1976	0.8002	0.7823	0.731	0.6028	0.5553	0.2507

1977	0.8566	0.826	0.7135	0.5491	0.4761	0.2132

1978	0.9891	0.957	0.8554	0.6722	0.6143	0.2699

1979	0.7568	0.7342	0.662	0.5459	0.518	0.2468

1980	1.011	0.9769	0.9095	0.7696	0.6744	0.2757

1981	0.5854	0.5662	0.4948	0.3887	0.3504	0.1713

1982	1.463	1.421	1.291	1.028	0.8628	0.3688

1983	1.581	1.532	1.34	1.148	0.9798	0.3904

1984	0.8696	0.8431	0.7484	0.6102	0.581	0.2776

1985	1.519	1.468	1.308	1.151	0.9894	0.4147

1986	1.306	1.263	1.126	0.944	0.8121	0.3898

1987	0.6673	0.6457	0.5998	0.5546	0.5373	0.2596

1988	0.668	0.6468	0.6073	0.5408	0.4721	0.2062

1989	2.052	1.986	1.909	1.515	1.293	0.507

1990	1.241	1.204	1.054	0.8966	0.7962	0.3758

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	2.052	1.986	1.909	1.515	1.293	0.507

0.0645161290322581	1.581	1.532	1.34	1.151	0.9894	0.4147

0.0967741935483871	1.519	1.468	1.308	1.148	0.9798	0.3904

0.129032258064516	1.463	1.421	1.291	1.028	0.9216	0.3898

0.161290322580645	1.367	1.338	1.178	1.012	0.8628	0.3787

0.193548387096774	1.325	1.281	1.163	0.9723	0.8423	0.3758

0.225806451612903	1.306	1.263	1.126	0.944	0.8121	0.3688

0.258064516129032	1.241	1.204	1.054	0.8966	0.7962	0.3407

0.290322580645161	1.07	1.034	0.9218	0.7696	0.6744	0.2896

0.32258064516129	1.011	0.9769	0.9095	0.7363	0.6492	0.2779

0.354838709677419	0.9891	0.957	0.8554	0.6937	0.6205	0.2776

0.387096774193548	0.8698	0.8431	0.7504	0.6722	0.6143	0.2757

0.419354838709677	0.8696	0.8417	0.7484	0.6102	0.581	0.2699

0.451612903225806	0.8566	0.826	0.731	0.6028	0.575	0.2613

0.483870967741936	0.8002	0.7823	0.7135	0.5801	0.5553	0.2596

0.516129032258065	0.7754	0.7508	0.6786	0.5664	0.5373	0.2573

0.548387096774194	0.7598	0.7356	0.662	0.5546	0.518	0.2507

0.580645161290323	0.7568	0.7342	0.6574	0.5491	0.4981	0.2491

0.612903225806452	0.7409	0.7146	0.6531	0.5459	0.483	0.2468

0.645161290322581	0.7365	0.712	0.6125	0.5408	0.4761	0.2456

0.67741935483871	0.6966	0.6741	0.6073	0.5322	0.4721	0.2132

0.709677419354839	0.668	0.6468	0.605	0.5174	0.4417	0.2129

0.741935483870968	0.6673	0.6457	0.5998	0.5047	0.4352	0.2098

0.774193548387097	0.6625	0.6422	0.5756	0.487	0.4233	0.2062

0.806451612903226	0.6433	0.6219	0.5642	0.4579	0.4128	0.1944

0.838709677419355	0.5862	0.5665	0.5314	0.4455	0.4094	0.1906

0.870967741935484	0.5854	0.5662	0.5014	0.4201	0.3771	0.1736

0.903225806451613	0.5779	0.5588	0.4948	0.3887	0.3504	0.1721

0.935483870967742	0.5752	0.5554	0.4892	0.381	0.3322	0.1713

0.967741935483871	0.5739	0.5546	0.481	0.3789	0.3258	0.1527

0.1	1.5134	1.4633	1.3063	1.136	0.97398	0.39034

					Average of yearly averages:	0.274126666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: PATOMAIR

Metfile:	w14751.dvf

PRZM scenario:	PAtomatoSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1098	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.05	fraction of application rate applied to pond

Application Date	Date	16-4	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	5	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1098	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

stored as PATOMGRD.out

Chemical: DPXE2Y45

PRZM environment: PAtomatoSTD.txt	modified Tueday, 29 May 2007 at
13:01:58

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w14751.dvf	modified Wedday, 3 July 2002 at 09:06:14

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.3808	0.367	0.3271	0.254	0.2144	0.09472

1962	0.2751	0.2659	0.2322	0.1891	0.1824	0.104

1963	0.1358	0.1313	0.1165	0.1051	0.1002	0.06169

1964	0.3968	0.3828	0.332	0.2903	0.2732	0.1222

1965	0.2099	0.2026	0.1771	0.1547	0.1483	0.08356

1966	0.6415	0.6191	0.5405	0.4121	0.3494	0.1628

1967	0.4442	0.4302	0.3809	0.3023	0.2744	0.1588

1968	1.169	1.146	1.008	0.7746	0.7248	0.2962

1969	0.698	0.6746	0.6048	0.4563	0.3805	0.1932

1970	0.242	0.2369	0.2218	0.1938	0.1949	0.1236

1971	0.3789	0.3674	0.3232	0.259	0.2216	0.1031

1972	0.5546	0.5378	0.4756	0.376	0.3693	0.17

1973	0.5887	0.5713	0.502	0.441	0.3985	0.1714

1974	0.7995	0.7716	0.6915	0.5581	0.4883	0.2065

1975	1.016	0.9823	0.8802	0.7388	0.642	0.2582

1976	0.5704	0.551	0.5103	0.4317	0.3699	0.1656

1977	0.4554	0.4392	0.3799	0.2868	0.2539	0.1223

1978	0.7172	0.6931	0.6179	0.4895	0.4236	0.1781

1979	0.5167	0.5009	0.4517	0.3812	0.3375	0.155

1980	0.7788	0.7519	0.6779	0.5447	0.4748	0.1928

1981	0.1573	0.1524	0.1386	0.124	0.1169	0.07991

1982	1.294	1.256	1.143	0.904	0.7562	0.286

1983	1.212	1.174	1.027	0.9156	0.7856	0.312

1984	0.6482	0.6275	0.558	0.4594	0.3906	0.1877

1985	1.288	1.245	1.105	0.9544	0.8241	0.3318

1986	0.8952	0.8664	0.8034	0.6852	0.5955	0.3044

1987	0.4982	0.4814	0.4183	0.3537	0.3285	0.1724

1988	0.4076	0.3942	0.352	0.2914	0.2522	0.1186

1989	1.808	1.75	1.684	1.34	1.135	0.4294

1990	1.039	1.007	0.8782	0.7095	0.6342	0.291

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	1.808	1.75	1.684	1.34	1.135	0.4294

0.0645161290322581	1.294	1.256	1.143	0.9544	0.8241	0.3318

0.0967741935483871	1.288	1.245	1.105	0.9156	0.7856	0.312

0.129032258064516	1.212	1.174	1.027	0.904	0.7562	0.3044

0.161290322580645	1.169	1.146	1.008	0.7746	0.7248	0.2962

0.193548387096774	1.039	1.007	0.8802	0.7388	0.642	0.291

0.225806451612903	1.016	0.9823	0.8782	0.7095	0.6342	0.286

0.258064516129032	0.8952	0.8664	0.8034	0.6852	0.5955	0.2582

0.290322580645161	0.7995	0.7716	0.6915	0.5581	0.4883	0.2065

0.32258064516129	0.7788	0.7519	0.6779	0.5447	0.4748	0.1932

0.354838709677419	0.7172	0.6931	0.6179	0.4895	0.4236	0.1928

0.387096774193548	0.698	0.6746	0.6048	0.4594	0.3985	0.1877

0.419354838709677	0.6482	0.6275	0.558	0.4563	0.3906	0.1781

0.451612903225806	0.6415	0.6191	0.5405	0.441	0.3805	0.1724

0.483870967741936	0.5887	0.5713	0.5103	0.4317	0.3699	0.1714

0.516129032258065	0.5704	0.551	0.502	0.4121	0.3693	0.17

0.548387096774194	0.5546	0.5378	0.4756	0.3812	0.3494	0.1656

0.580645161290323	0.5167	0.5009	0.4517	0.376	0.3375	0.1628

0.612903225806452	0.4982	0.4814	0.4183	0.3537	0.3285	0.1588

0.645161290322581	0.4554	0.4392	0.3809	0.3023	0.2744	0.155

0.67741935483871	0.4442	0.4302	0.3799	0.2914	0.2732	0.1236

0.709677419354839	0.4076	0.3942	0.352	0.2903	0.2539	0.1223

0.741935483870968	0.3968	0.3828	0.332	0.2868	0.2522	0.1222

0.774193548387097	0.3808	0.3674	0.3271	0.259	0.2216	0.1186

0.806451612903226	0.3789	0.367	0.3232	0.254	0.2144	0.104

0.838709677419355	0.2751	0.2659	0.2322	0.1938	0.1949	0.1031

0.870967741935484	0.242	0.2369	0.2218	0.1891	0.1824	0.09472

0.903225806451613	0.2099	0.2026	0.1771	0.1547	0.1483	0.08356

0.935483870967742	0.1573	0.1524	0.1386	0.124	0.1169	0.07991

0.967741935483871	0.1358	0.1313	0.1165	0.1051	0.1002	0.06169

0.1	1.2804	1.2379	1.0972	0.91444	0.78266	0.31124

					Average of yearly averages:	0.187899333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: PATOMGRD

Metfile:	w14751.dvf

PRZM scenario:	PAtomatoSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1098	kg/ha

Application Efficiency:	APPEFF	0.99	fraction

Spray Drift	DRFT	0.01	fraction of application rate applied to pond

Application Date	Date	16-4	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	5	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1098	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

PA Turf

stored as PATURFGRD.out

Chemical: DPXE2Y45

PRZM environment: PAturfSTD.txt	modified Thuday, 23 February 2006 at
17:55:08

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w14751.dvf	modified Wedday, 3 July 2002 at 09:06:14

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.4253	0.4114	0.3603	0.2833	0.2397	0.1146

1962	0.3165	0.3059	0.2674	0.2095	0.182	0.08824

1963	0.2965	0.2858	0.247	0.1907	0.1614	0.06915

1964	0.294	0.2844	0.2491	0.2024	0.1797	0.07783

1965	0.2913	0.2818	0.2469	0.1922	0.1637	0.06853

1966	0.8803	0.849	0.735	0.5503	0.4626	0.1854

1967	0.4118	0.3995	0.354	0.3106	0.2748	0.1773

1968	0.9551	0.9244	0.8029	0.6043	0.5078	0.2339

1969	0.924	0.8929	0.8017	0.6025	0.5013	0.2397

1970	1.136	1.097	1.015	0.7874	0.6631	0.2875

1971	0.3167	0.3059	0.2663	0.2183	0.1915	0.1098

1972	0.4512	0.4371	0.3836	0.2961	0.2489	0.1334

1973	0.3822	0.3699	0.3251	0.275	0.2613	0.1189

1974	0.3412	0.3302	0.2897	0.258	0.2368	0.1102

1975	0.475	0.4598	0.4085	0.3423	0.3126	0.1374

1976	0.3013	0.2901	0.2568	0.2327	0.2199	0.1037

1977	0.3274	0.3156	0.2741	0.2137	0.1815	0.07849

1978	0.3934	0.383	0.3369	0.2717	0.2547	0.1197

1979	0.3038	0.2939	0.2576	0.2138	0.1953	0.09628

1980	0.3223	0.3113	0.274	0.2568	0.2337	0.09964

1981	0.2976	0.2877	0.2514	0.1962	0.1672	0.07563

1982	0.9944	0.9606	0.8588	0.6763	0.5657	0.2356

1983	1.178	1.142	1.079	0.8658	0.7317	0.2887

1984	0.5239	0.5086	0.4485	0.3709	0.3746	0.1842

1985	0.576	0.5571	0.4877	0.4244	0.371	0.1712

1986	0.8135	0.7876	0.687	0.5181	0.4393	0.1963

1987	0.3207	0.3108	0.2745	0.2181	0.2075	0.1135

1988	0.3015	0.2915	0.2548	0.2006	0.1716	0.07746

1989	1.114	1.089	0.9985	0.7796	0.659	0.2633

1990	0.7021	0.6802	0.5934	0.4575	0.3989	0.2

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	1.178	1.142	1.079	0.8658	0.7317	0.2887

0.0645161290322581	1.136	1.097	1.015	0.7874	0.6631	0.2875

0.0967741935483871	1.114	1.089	0.9985	0.7796	0.659	0.2633

0.129032258064516	0.9944	0.9606	0.8588	0.6763	0.5657	0.2397

0.161290322580645	0.9551	0.9244	0.8029	0.6043	0.5078	0.2356

0.193548387096774	0.924	0.8929	0.8017	0.6025	0.5013	0.2339

0.225806451612903	0.8803	0.849	0.735	0.5503	0.4626	0.2

0.258064516129032	0.8135	0.7876	0.687	0.5181	0.4393	0.1963

0.290322580645161	0.7021	0.6802	0.5934	0.4575	0.3989	0.1854

0.32258064516129	0.576	0.5571	0.4877	0.4244	0.3746	0.1842

0.354838709677419	0.5239	0.5086	0.4485	0.3709	0.371	0.1773

0.387096774193548	0.475	0.4598	0.4085	0.3423	0.3126	0.1712

0.419354838709677	0.4512	0.4371	0.3836	0.3106	0.2748	0.1374

0.451612903225806	0.4253	0.4114	0.3603	0.2961	0.2613	0.1334

0.483870967741936	0.4118	0.3995	0.354	0.2833	0.2547	0.1197

0.516129032258065	0.3934	0.383	0.3369	0.275	0.2489	0.1189

0.548387096774194	0.3822	0.3699	0.3251	0.2717	0.2397	0.1146

0.580645161290323	0.3412	0.3302	0.2897	0.258	0.2368	0.1135

0.612903225806452	0.3274	0.3156	0.2745	0.2568	0.2337	0.1102

0.645161290322581	0.3223	0.3113	0.2741	0.2327	0.2199	0.1098

0.67741935483871	0.3207	0.3108	0.274	0.2183	0.2075	0.1037

0.709677419354839	0.3167	0.3059	0.2674	0.2181	0.1953	0.09964

0.741935483870968	0.3165	0.3059	0.2663	0.2138	0.1915	0.09628

0.774193548387097	0.3038	0.2939	0.2576	0.2137	0.182	0.08824

0.806451612903226	0.3015	0.2915	0.2568	0.2095	0.1815	0.07849

0.838709677419355	0.3013	0.2901	0.2548	0.2024	0.1797	0.07783

0.870967741935484	0.2976	0.2877	0.2514	0.2006	0.1716	0.07746

0.903225806451613	0.2965	0.2858	0.2491	0.1962	0.1672	0.07563

0.935483870967742	0.294	0.2844	0.247	0.1922	0.1637	0.06915

0.967741935483871	0.2913	0.2818	0.2469	0.1907	0.1614	0.06853

0.1	1.10204	1.07616	0.98453	0.76927	0.64967	0.26094

					Average of yearly averages:	0.148518333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: PATURFGRD

Metfile:	w14751.dvf

PRZM scenario:	PAturfSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.2912	kg/ha

Application Efficiency:	APPEFF	0.99	fraction

Spray Drift	DRFT	0.01	fraction of application rate applied to pond

Application Date	Date	1-4	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	7	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.2912	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

stored as PATF19GRD.out

Chemical: DPXE2Y45

PRZM environment: PAturfSTD.txt	modified Thuday, 23 February 2006 at
16:55:08

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
15:33:30

Metfile: w14751.dvf	modified Wedday, 3 July 2002 at 08:06:14

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.9077	0.8775	0.7875	0.6933	0.6087	0.2272

1962	0.4104	0.3965	0.3457	0.2731	0.2526	0.2038

1963	0.1591	0.1544	0.1447	0.1444	0.1388	0.1231

1964	0.2163	0.2093	0.1988	0.182	0.175	0.1213

1965	0.1859	0.1799	0.1654	0.1434	0.1349	0.09031

1966	1.675	1.615	1.398	1.045	0.8785	0.2988

1967	0.7861	0.7752	0.6902	0.58	0.5302	0.3504

1968	0.9875	0.9503	0.8157	0.6261	0.5405	0.3486

1969	2.564	2.483	2.22	1.671	1.388	0.5766

1970	0.5023	0.5023	0.5022	0.4994	0.4762	0.3248

1971	1.17	1.133	0.9749	0.7988	0.6851	0.2815

1972	4.064	3.933	3.432	2.619	2.196	0.8335

1973	1.135	1.096	0.9547	0.7333	0.626	0.4423

1974	0.5937	0.5805	0.5165	0.4804	0.4289	0.2641

1975	0.6043	0.5839	0.5271	0.428	0.3671	0.2429

1976	0.3859	0.3733	0.3402	0.2712	0.2467	0.18

1977	0.1456	0.1416	0.138	0.1363	0.1336	0.1066

1978	0.5422	0.5236	0.4731	0.3998	0.3439	0.1649

1979	0.2771	0.2685	0.2491	0.2193	0.2173	0.1437

1980	0.2645	0.2561	0.238	0.2236	0.1883	0.1375

1981	0.3059	0.2986	0.2715	0.2344	0.208	0.1566

1982	1.069	1.039	0.9845	0.8234	0.7108	0.2874

1983	0.3862	0.3745	0.3461	0.3152	0.2979	0.161

1984	0.4911	0.4753	0.4456	0.4182	0.376	0.1723

1985	0.2824	0.273	0.2418	0.2166	0.205	0.1474

1986	0.8683	0.8389	0.7316	0.5608	0.4769	0.2441

1987	0.4696	0.453	0.4099	0.335	0.3048	0.2023

1988	0.4079	0.3932	0.3535	0.272	0.2302	0.142

1989	0.6636	0.643	0.5673	0.4995	0.4658	0.2533

1990	0.7076	0.6852	0.6132	0.5206	0.4787	0.2569

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	4.064	3.933	3.432	2.619	2.196	0.8335

0.0645161290322581	2.564	2.483	2.22	1.671	1.388	0.5766

0.0967741935483871	1.675	1.615	1.398	1.045	0.8785	0.4423

0.129032258064516	1.17	1.133	0.9845	0.8234	0.7108	0.3504

0.161290322580645	1.135	1.096	0.9749	0.7988	0.6851	0.3486

0.193548387096774	1.069	1.039	0.9547	0.7333	0.626	0.3248

0.225806451612903	0.9875	0.9503	0.8157	0.6933	0.6087	0.2988

0.258064516129032	0.9077	0.8775	0.7875	0.6261	0.5405	0.2874

0.290322580645161	0.8683	0.8389	0.7316	0.58	0.5302	0.2815

0.32258064516129	0.7861	0.7752	0.6902	0.5608	0.4787	0.2641

0.354838709677419	0.7076	0.6852	0.6132	0.5206	0.4769	0.2569

0.387096774193548	0.6636	0.643	0.5673	0.4995	0.4762	0.2533

0.419354838709677	0.6043	0.5839	0.5271	0.4994	0.4658	0.2441

0.451612903225806	0.5937	0.5805	0.5165	0.4804	0.4289	0.2429

0.483870967741936	0.5422	0.5236	0.5022	0.428	0.376	0.2272

0.516129032258065	0.5023	0.5023	0.4731	0.4182	0.3671	0.2038

0.548387096774194	0.4911	0.4753	0.4456	0.3998	0.3439	0.2023

0.580645161290323	0.4696	0.453	0.4099	0.335	0.3048	0.18

0.612903225806452	0.4104	0.3965	0.3535	0.3152	0.2979	0.1723

0.645161290322581	0.4079	0.3932	0.3461	0.2731	0.2526	0.1649

0.67741935483871	0.3862	0.3745	0.3457	0.272	0.2467	0.161

0.709677419354839	0.3859	0.3733	0.3402	0.2712	0.2302	0.1566

0.741935483870968	0.3059	0.2986	0.2715	0.2344	0.2173	0.1474

0.774193548387097	0.2824	0.273	0.2491	0.2236	0.208	0.1437

0.806451612903226	0.2771	0.2685	0.2418	0.2193	0.205	0.142

0.838709677419355	0.2645	0.2561	0.238	0.2166	0.1883	0.1375

0.870967741935484	0.2163	0.2093	0.1988	0.182	0.175	0.1231

0.903225806451613	0.1859	0.1799	0.1654	0.1444	0.1388	0.1213

0.935483870967742	0.1591	0.1544	0.1447	0.1434	0.1349	0.1066

0.967741935483871	0.1456	0.1416	0.138	0.1363	0.1336	0.09031

0.1	1.6245	1.5668	1.35665	1.02284	0.86173	0.43311

					Average of yearly averages:	0.249507

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: PATF19GRD

Metfile:	w14751.dvf

PRZM scenario:	PAturfSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.029	kg/ha

Application Efficiency:	APPEFF	0.99	fraction

Spray Drift	DRFT	0.01	fraction of application rate applied to pond

Application Date	Date	1-4	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	7	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.029	kg/ha

Interval 2	interval	7	days	Set to 0 or delete line for single app.

app. rate 2	apprate	0.029	kg/ha

Interval 3	interval	7	days	Set to 0 or delete line for single app.

app. rate 3	apprate	0.029	kg/ha

Interval 4	interval	7	days	Set to 0 or delete line for single app.

app. rate 4	apprate	0.029	kg/ha

Interval 5	interval	7	days	Set to 0 or delete line for single app.

app. rate 5	apprate	0.029	kg/ha

Interval 6	interval	7	days	Set to 0 or delete line for single app.

app. rate 6	apprate	0.029	kg/ha

Interval 7	interval	7	days	Set to 0 or delete line for single app.

app. rate 7	apprate	0.029	kg/ha

Interval 8	interval	7	days	Set to 0 or delete line for single app.

app. rate 8	apprate	0.029	kg/ha

Interval 9	interval	7	days	Set to 0 or delete line for single app.

app. rate 9	apprate	0.029	kg/ha

Interval 10	interval	7	days	Set to 0 or delete line for single app.

app. rate 10	apprate	0.029	kg/ha

Interval 11	interval	7	days	Set to 0 or delete line for single app.

app. rate 11	apprate	0.029	kg/ha

Interval 12	interval	7	days	Set to 0 or delete line for single app.

app. rate 12	apprate	0.029	kg/ha

Interval 13	interval	7	days	Set to 0 or delete line for single app.

app. rate 13	apprate	0.029	kg/ha

Interval 14	interval	7	days	Set to 0 or delete line for single app.

app. rate 14	apprate	0.029	kg/ha

Interval 15	interval	7	days	Set to 0 or delete line for single app.

app. rate 15	apprate	0.029	kg/ha

Interval 16	interval	7	days	Set to 0 or delete line for single app.

app. rate 16	apprate	0.029	kg/ha

Interval 17	interval	7	days	Set to 0 or delete line for single app.

app. rate 17	apprate	0.029	kg/ha

Interval 18	interval	7	days	Set to 0 or delete line for single app.

app. rate 18	apprate	0.029	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

Spray Drift Analysis

CA Cotton

stored as CACOTAIR.out

Chemical: DPXE2Y45

PRZM environment: CAcotton_WirrigSTD.txt	modified Tueday, 29 May 2007 at
12:42:12

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w93193.dvf	modified Wedday, 3 July 2002 at 09:04:24

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.03077	0.02947	0.02485	0.02033	0.01786	0.006117

1962	0.05288	0.05088	0.04335	0.03238	0.0296	0.01089

1963	0.7594	0.7297	0.6692	0.5503	0.4679	0.1593

1964	0.02927	0.02884	0.02714	0.02316	0.02044	0.008905

1965	2.52	2.419	2.063	1.557	1.271	0.4181

1966	0.0617	0.06073	0.05681	0.04902	0.04376	0.01838

1967	0.5374	0.5172	0.4471	0.3482	0.2881	0.09584

1968	0.3215	0.3132	0.281	0.2175	0.1936	0.07089

1969	2.083	2.013	1.72	1.258	1.034	0.3473

1970	1.334	1.279	1.134	0.8225	0.6674	0.2238

1971	0.4627	0.4433	0.3744	0.2725	0.22	0.07941

1972	0.0144	0.01425	0.01365	0.01209	0.01076	0.004662

1973	0.3525	0.3412	0.3052	0.2443	0.2008	0.06653

1974	0.231	0.2225	0.1916	0.1761	0.1485	0.051

1975	0.05049	0.0487	0.04219	0.03143	0.02577	0.00962

1976	0.04331	0.04152	0.03511	0.02556	0.02085	0.007328

1977	0.1711	0.1642	0.1459	0.1092	0.09109	0.03048

1978	0.6844	0.6591	0.5767	0.4374	0.3593	0.1183

1979	0.3242	0.3123	0.2938	0.229	0.1887	0.06432

1980	1.291	1.249	1.148	0.9099	0.7604	0.2587

1981	0.1392	0.1345	0.1166	0.0867	0.07431	0.02978

1982	0.3506	0.3415	0.3034	0.224	0.1815	0.06051

1983	0.5535	0.5339	0.4676	0.3561	0.2936	0.09992

1984	0.01308	0.0129	0.01217	0.01053	0.009328	0.003981

1985	0.04681	0.04492	0.03823	0.02738	0.02206	0.007185

1986	0.5331	0.5174	0.4742	0.3512	0.3053	0.1071

1987	0.6987	0.6713	0.6011	0.4498	0.3667	0.1222

1988	0.4243	0.4109	0.3603	0.2823	0.2799	0.1066

1989	1.023	0.986	0.8421	0.739	0.6269	0.2137

1990	0.1842	0.1766	0.1489	0.1062	0.08525	0.03244

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	2.52	2.419	2.063	1.557	1.271	0.4181

0.0645161290322581	2.083	2.013	1.72	1.258	1.034	0.3473

0.0967741935483871	1.334	1.279	1.148	0.9099	0.7604	0.2587

0.129032258064516	1.291	1.249	1.134	0.8225	0.6674	0.2238

0.161290322580645	1.023	0.986	0.8421	0.739	0.6269	0.2137

0.193548387096774	0.7594	0.7297	0.6692	0.5503	0.4679	0.1593

0.225806451612903	0.6987	0.6713	0.6011	0.4498	0.3667	0.1222

0.258064516129032	0.6844	0.6591	0.5767	0.4374	0.3593	0.1183

0.290322580645161	0.5535	0.5339	0.4742	0.3561	0.3053	0.1071

0.32258064516129	0.5374	0.5174	0.4676	0.3512	0.2936	0.1066

0.354838709677419	0.5331	0.5172	0.4471	0.3482	0.2881	0.09992

0.387096774193548	0.4627	0.4433	0.3744	0.2823	0.2799	0.09584

0.419354838709677	0.4243	0.4109	0.3603	0.2725	0.22	0.07941

0.451612903225806	0.3525	0.3415	0.3052	0.2443	0.2008	0.07089

0.483870967741936	0.3506	0.3412	0.3034	0.229	0.1936	0.06653

0.516129032258065	0.3242	0.3132	0.2938	0.224	0.1887	0.06432

0.548387096774194	0.3215	0.3123	0.281	0.2175	0.1815	0.06051

0.580645161290323	0.231	0.2225	0.1916	0.1761	0.1485	0.051

0.612903225806452	0.1842	0.1766	0.1489	0.1092	0.09109	0.03244

0.645161290322581	0.1711	0.1642	0.1459	0.1062	0.08525	0.03048

0.67741935483871	0.1392	0.1345	0.1166	0.0867	0.07431	0.02978

0.709677419354839	0.0617	0.06073	0.05681	0.04902	0.04376	0.01838

0.741935483870968	0.05288	0.05088	0.04335	0.03238	0.0296	0.01089

0.774193548387097	0.05049	0.0487	0.04219	0.03143	0.02577	0.00962

0.806451612903226	0.04681	0.04492	0.03823	0.02738	0.02206	0.008905

0.838709677419355	0.04331	0.04152	0.03511	0.02556	0.02085	0.007328

0.870967741935484	0.03077	0.02947	0.02714	0.02316	0.02044	0.007185

0.903225806451613	0.02927	0.02884	0.02485	0.02033	0.01786	0.006117

0.935483870967742	0.0144	0.01425	0.01365	0.01209	0.01076	0.004662

0.967741935483871	0.01308	0.0129	0.01217	0.01053	0.009328	0.003981

0.1	1.3297	1.276	1.1466	0.90116	0.7511	0.25521

					Average of yearly averages:	0.0944429333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CACOTAIR

Metfile:	w93193.dvf

PRZM scenario:	CAcotton_WirrigSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1109	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.00	fraction of application rate applied to pond

Application Date	Date	16-2	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	5	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1109	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

CA Grape

stored as CAGRAPAIR.out

Chemical: DPXE2Y45

PRZM environment: CAgrapes_WirrigSTD.txt	modified Tueday, 29 May 2007 at
12:42:54

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w93193.dvf	modified Wedday, 3 July 2002 at 09:04:24

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.002715	0.002605	0.002239	0.001644	0.001336	0.0004327

1962	0.3327	0.3222	0.2848	0.2115	0.1725	0.05747

1963	0.1398	0.1349	0.1214	0.09716	0.08596	0.03177

1964	0.00501	0.004853	0.004362	0.003666	0.003737	0.001651

1965	0.2897	0.278	0.2363	0.1744	0.142	0.04659

1966	0.006831	0.006723	0.00629	0.005427	0.004847	0.002003

1967	0.04427	0.0431	0.03759	0.03259	0.0287	0.0102

1968	0.009641	0.009247	0.007863	0.006833	0.005723	0.002183

1969	0.2139	0.2066	0.1763	0.1286	0.1051	0.03537

1970	0.1259	0.122	0.1058	0.07652	0.06207	0.0208

1971	0.00335	0.003232	0.002804	0.002146	0.001831	0.00109

1972	0.0005321	0.0005107	0.0004647	0.000366	0.000315	0.0001357

1973	0.1552	0.1498	0.13	0.09936	0.08214	0.02753

1974	0.008977	0.008677	0.007466	0.005519	0.004497	0.002022

1975	0.0005458	0.0005294	0.0004694	0.0003799	0.0003288	0.0001527

1976	0.1916	0.1844	0.1581	0.1179	0.09714	0.03281

1977	0.01012	0.009757	0.008725	0.006895	0.00578	0.002433

1978	0.2407	0.2363	0.2095	0.1633	0.1367	0.04613

1979	0.02609	0.02519	0.02187	0.01651	0.01365	0.005147

1980	0.3072	0.2962	0.2575	0.1919	0.1575	0.05291

1981	0.03259	0.03144	0.02713	0.01996	0.01629	0.006257

1982	0.04139	0.03998	0.03652	0.02882	0.02356	0.007925

1983	0.1362	0.1314	0.1138	0.09589	0.08126	0.02815

1984	0.005313	0.005149	0.004548	0.003638	0.003348	0.001427

1985	0.003771	0.003631	0.003148	0.002901	0.002544	0.0009049

1986	0.2601	0.2504	0.2164	0.1671	0.1382	0.04605

1987	0.02534	0.02441	0.02111	0.01647	0.0137	0.00518

1988	0.01685	0.01611	0.01344	0.00975	0.008069	0.002752

1989	0.01837	0.01768	0.01515	0.01097	0.009519	0.003356

1990	0.0152	0.01459	0.01242	0.009086	0.007481	0.002566

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	0.3327	0.3222	0.2848	0.2115	0.1725	0.05747

0.0645161290322581	0.3072	0.2962	0.2575	0.1919	0.1575	0.05291

0.0967741935483871	0.2897	0.278	0.2363	0.1744	0.142	0.04659

0.129032258064516	0.2601	0.2504	0.2164	0.1671	0.1382	0.04613

0.161290322580645	0.2407	0.2363	0.2095	0.1633	0.1367	0.04605

0.193548387096774	0.2139	0.2066	0.1763	0.1286	0.1051	0.03537

0.225806451612903	0.1916	0.1844	0.1581	0.1179	0.09714	0.03281

0.258064516129032	0.1552	0.1498	0.13	0.09936	0.08596	0.03177

0.290322580645161	0.1398	0.1349	0.1214	0.09716	0.08214	0.02815

0.32258064516129	0.1362	0.1314	0.1138	0.09589	0.08126	0.02753

0.354838709677419	0.1259	0.122	0.1058	0.07652	0.06207	0.0208

0.387096774193548	0.04427	0.0431	0.03759	0.03259	0.0287	0.0102

0.419354838709677	0.04139	0.03998	0.03652	0.02882	0.02356	0.007925

0.451612903225806	0.03259	0.03144	0.02713	0.01996	0.01629	0.006257

0.483870967741936	0.02609	0.02519	0.02187	0.01651	0.0137	0.00518

0.516129032258065	0.02534	0.02441	0.02111	0.01647	0.01365	0.005147

0.548387096774194	0.01837	0.01768	0.01515	0.01097	0.009519	0.003356

0.580645161290323	0.01685	0.01611	0.01344	0.00975	0.008069	0.002752

0.612903225806452	0.0152	0.01459	0.01242	0.009086	0.007481	0.002566

0.645161290322581	0.01012	0.009757	0.008725	0.006895	0.00578	0.002433

0.67741935483871	0.009641	0.009247	0.007863	0.006833	0.005723	0.002183

0.709677419354839	0.008977	0.008677	0.007466	0.005519	0.004847	0.002022

0.741935483870968	0.006831	0.006723	0.00629	0.005427	0.004497	0.002003

0.774193548387097	0.005313	0.005149	0.004548	0.003666	0.003737	0.001651

0.806451612903226	0.00501	0.004853	0.004362	0.003638	0.003348	0.001427

0.838709677419355	0.003771	0.003631	0.003148	0.002901	0.002544	0.00109

0.870967741935484	0.00335	0.003232	0.002804	0.002146	0.001831	0.0009049

0.903225806451613	0.002715	0.002605	0.002239	0.001644	0.001336	0.0004327

0.935483870967742	0.0005458	0.0005294	0.0004694	0.0003799	0.0003288
0.0001527

0.967741935483871	0.0005321	0.0005107	0.0004647	0.000366	0.000315
0.0001357

0.1	0.28674	0.27524	0.23431	0.17367	0.14162	0.046544

					Average of yearly averages:	0.0161132666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CAGRAPAIR

Metfile:	w93193.dvf

PRZM scenario:	CAgrapes_WirrigSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1109	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.00	fraction of application rate applied to pond

Application Date	Date	1-2	dd/mm or dd/mmm or dd-mm or dd-mmm

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

CA Lettuce

stored as CALETAIR.out

Chemical: DPXE2Y45

PRZM environment: CAlettuceSTD.txt	modified Tueday, 21 February 2006 at
14:38:22

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w23273.dvf	modified Wedday, 3 July 2002 at 09:04:22

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	1.963	1.903	1.627	0.996	0.6642	0.1649

1962	1.493	1.448	1.289	1.07	1.021	0.4444

1963	2.218	2.13	1.909	1.591	1.353	0.5199

1964	0.6549	0.6294	0.5477	0.436	0.3647	0.2074

1965	0.6151	0.594	0.5231	0.3946	0.3334	0.1636

1966	1.319	1.267	1.098	0.8	0.5346	0.1461

1967	0.7983	0.7712	0.6723	0.6121	0.5773	0.2749

1968	0.72	0.6919	0.5958	0.4568	0.376	0.1911

1969	3.092	2.979	2.6	1.902	1.569	0.5841

1970	3.879	3.715	3.305	2.392	1.941	0.7143

1971	0.5941	0.5728	0.4914	0.363	0.2993	0.1739

1972	1.508	1.45	1.257	0.9084	0.6749	0.1963

1973	0.9311	0.9053	0.8052	0.709	0.6102	0.3102

1974	3.525	3.409	3.048	2.338	1.929	0.6985

1975	1.234	1.187	1.025	0.7667	0.6358	0.2543

1976	0.7907	0.7666	0.6598	0.5316	0.4704	0.2352

1977	1.225	1.185	1.023	0.7796	0.8003	0.3605

1978	2.605	2.508	2.203	1.665	1.377	0.5237

1979	0.9513	0.915	0.8017	0.6919	0.5941	0.2269

1980	1.33	1.293	1.185	0.9598	0.8019	0.3027

1981	2.95	2.855	2.501	1.922	1.589	0.5807

1982	0.6106	0.5902	0.5217	0.4454	0.3789	0.1514

1983	1.76	1.697	1.497	1.145	0.9536	0.3392

1984	0.5581	0.5378	0.4737	0.355	0.2464	0.08255

1985	0.498	0.4788	0.4334	0.3297	0.2545	0.158

1986	1.697	1.636	1.443	1.144	0.9567	0.3773

1987	2.997	2.892	2.467	1.802	1.479	0.542

1988	1.643	1.571	1.311	0.9905	0.8791	0.3476

1989	0.1143	0.1108	0.09777	0.07777	0.06906	0.04142

1990	0.2746	0.2636	0.2269	0.2145	0.1893	0.08629

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	3.879	3.715	3.305	2.392	1.941	0.7143

0.0645161290322581	3.525	3.409	3.048	2.338	1.929	0.6985

0.0967741935483871	3.092	2.979	2.6	1.922	1.589	0.5841

0.129032258064516	2.997	2.892	2.501	1.902	1.569	0.5807

0.161290322580645	2.95	2.855	2.467	1.802	1.479	0.542

0.193548387096774	2.605	2.508	2.203	1.665	1.377	0.5237

0.225806451612903	2.218	2.13	1.909	1.591	1.353	0.5199

0.258064516129032	1.963	1.903	1.627	1.145	1.021	0.4444

0.290322580645161	1.76	1.697	1.497	1.144	0.9567	0.3773

0.32258064516129	1.697	1.636	1.443	1.07	0.9536	0.3605

0.354838709677419	1.643	1.571	1.311	0.996	0.8791	0.3476

0.387096774193548	1.508	1.45	1.289	0.9905	0.8019	0.3392

0.419354838709677	1.493	1.448	1.257	0.9598	0.8003	0.3102

0.451612903225806	1.33	1.293	1.185	0.9084	0.6749	0.3027

0.483870967741936	1.319	1.267	1.098	0.8	0.6642	0.2749

0.516129032258065	1.234	1.187	1.025	0.7796	0.6358	0.2543

0.548387096774194	1.225	1.185	1.023	0.7667	0.6102	0.2352

0.580645161290323	0.9513	0.915	0.8052	0.709	0.5941	0.2269

0.612903225806452	0.9311	0.9053	0.8017	0.6919	0.5773	0.2074

0.645161290322581	0.7983	0.7712	0.6723	0.6121	0.5346	0.1963

0.67741935483871	0.7907	0.7666	0.6598	0.5316	0.4704	0.1911

0.709677419354839	0.72	0.6919	0.5958	0.4568	0.3789	0.1739

0.741935483870968	0.6549	0.6294	0.5477	0.4454	0.376	0.1649

0.774193548387097	0.6151	0.594	0.5231	0.436	0.3647	0.1636

0.806451612903226	0.6106	0.5902	0.5217	0.3946	0.3334	0.158

0.838709677419355	0.5941	0.5728	0.4914	0.363	0.2993	0.1514

0.870967741935484	0.5581	0.5378	0.4737	0.355	0.2545	0.1461

0.903225806451613	0.498	0.4788	0.4334	0.3297	0.2464	0.08629

0.935483870967742	0.2746	0.2636	0.2269	0.2145	0.1893	0.08255

0.967741935483871	0.1143	0.1108	0.09777	0.07777	0.06906	0.04142

0.1	3.0825	2.9703	2.5901	1.92	1.587	0.58376

					Average of yearly averages:	0.313312

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CALETAIR

Metfile:	w23273.dvf

PRZM scenario:	CAlettuceSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.0728	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.00	fraction of application rate applied to pond

Application Date	Date	16-2	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	3	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.0728	kg/ha

Interval 2	interval	3	days	Set to 0 or delete line for single app.

app. rate 2	apprate	0.0728	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

CA Tomato

stored as CATOMAIR.out

Chemical: DPXE2Y45

PRZM environment: CAtomato_WirrigSTD.txt	modified Tueday, 29 May 2007 at
12:43:54

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w93193.dvf	modified Wedday, 3 July 2002 at 09:04:24

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.01475	0.01416	0.01194	0.00895	0.007308	0.002414

1962	0.04922	0.04724	0.03988	0.02825	0.0228	0.007376

1963	0.3763	0.3628	0.3444	0.2863	0.2478	0.08563

1964	0.01615	0.01592	0.01498	0.01278	0.0115	0.00487

1965	1.542	1.48	1.262	0.9489	0.7747	0.2546

1966	0.03755	0.03695	0.03457	0.02983	0.02678	0.01101

1967	0.3427	0.3298	0.2899	0.2549	0.2154	0.07285

1968	0.2595	0.2518	0.225	0.1838	0.1511	0.05134

1969	0.2554	0.2448	0.2068	0.1476	0.1277	0.04641

1970	0.6329	0.6066	0.5336	0.3877	0.3144	0.1034

1971	0.05563	0.05351	0.04591	0.0397	0.03608	0.01479

1972	0.003076	0.002968	0.002657	0.002142	0.001958	0.001082

1973	0.2742	0.2645	0.2271	0.1622	0.1307	0.04215

1974	0.111	0.1081	0.09555	0.06954	0.06026	0.02202

1975	0.03937	0.03795	0.03276	0.02424	0.01974	0.006938

1976	0.003359	0.003232	0.002771	0.002066	0.001722	0.0007385

1977	0.08814	0.08456	0.07754	0.05686	0.04643	0.01523

1978	0.4076	0.3933	0.3655	0.3061	0.2694	0.09309

1979	0.07222	0.06976	0.0606	0.05083	0.04358	0.01689

1980	0.5507	0.5285	0.4487	0.3262	0.2662	0.088

1981	0.2519	0.2425	0.2079	0.1518	0.1232	0.04162

1982	0.4257	0.4152	0.377	0.2938	0.2399	0.0803

1983	0.5044	0.4879	0.4693	0.3912	0.3314	0.1144

1984	0.01597	0.01575	0.01486	0.01286	0.0118	0.005

1985	0.01404	0.01349	0.01167	0.008458	0.006833	0.002305

1986	0.6348	0.6104	0.5246	0.3976	0.3242	0.1051

1987	0.2284	0.2199	0.189	0.1576	0.1312	0.04582

1988	0.03004	0.0291	0.02529	0.01895	0.01551	0.00615

1989	0.4059	0.3907	0.3321	0.2451	0.2141	0.0739

1990	0.01039	0.01003	0.008733	0.007605	0.00687	0.003967

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	1.542	1.48	1.262	0.9489	0.7747	0.2546

0.0645161290322581	0.6348	0.6104	0.5336	0.3976	0.3314	0.1144

0.0967741935483871	0.6329	0.6066	0.5246	0.3912	0.3242	0.1051

0.129032258064516	0.5507	0.5285	0.4693	0.3877	0.3144	0.1034

0.161290322580645	0.5044	0.4879	0.4487	0.3262	0.2694	0.09309

0.193548387096774	0.4257	0.4152	0.377	0.3061	0.2662	0.088

0.225806451612903	0.4076	0.3933	0.3655	0.2938	0.2478	0.08563

0.258064516129032	0.4059	0.3907	0.3444	0.2863	0.2399	0.0803

0.290322580645161	0.3763	0.3628	0.3321	0.2549	0.2154	0.0739

0.32258064516129	0.3427	0.3298	0.2899	0.2451	0.2141	0.07285

0.354838709677419	0.2742	0.2645	0.2271	0.1838	0.1511	0.05134

0.387096774193548	0.2595	0.2518	0.225	0.1622	0.1312	0.04641

0.419354838709677	0.2554	0.2448	0.2079	0.1576	0.1307	0.04582

0.451612903225806	0.2519	0.2425	0.2068	0.1518	0.1277	0.04215

0.483870967741936	0.2284	0.2199	0.189	0.1476	0.1232	0.04162

0.516129032258065	0.111	0.1081	0.09555	0.06954	0.06026	0.02202

0.548387096774194	0.08814	0.08456	0.07754	0.05686	0.04643	0.01689

0.580645161290323	0.07222	0.06976	0.0606	0.05083	0.04358	0.01523

0.612903225806452	0.05563	0.05351	0.04591	0.0397	0.03608	0.01479

0.645161290322581	0.04922	0.04724	0.03988	0.02983	0.02678	0.01101

0.67741935483871	0.03937	0.03795	0.03457	0.02825	0.0228	0.007376

0.709677419354839	0.03755	0.03695	0.03276	0.02424	0.01974	0.006938

0.741935483870968	0.03004	0.0291	0.02529	0.01895	0.01551	0.00615

0.774193548387097	0.01615	0.01592	0.01498	0.01286	0.0118	0.005

0.806451612903226	0.01597	0.01575	0.01486	0.01278	0.0115	0.00487

0.838709677419355	0.01475	0.01416	0.01194	0.00895	0.007308	0.003967

0.870967741935484	0.01404	0.01349	0.01167	0.008458	0.00687	0.002414

0.903225806451613	0.01039	0.01003	0.008733	0.007605	0.006833	0.002305

0.935483870967742	0.003359	0.003232	0.002771	0.002142	0.001958	0.001082

0.967741935483871	0.003076	0.002968	0.002657	0.002066	0.001722	0.0007385

0.1	0.62468	0.59879	0.51907	0.39085	0.32322	0.10493

					Average of yearly averages:	0.0473130166666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CATOMAIR

Metfile:	w93193.dvf

PRZM scenario:	CAtomato_WirrigSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1098	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.00	fraction of application rate applied to pond

Application Date	Date	1-3	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	5	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1098	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

FL Cabbage

stored as FLCABAIR.out

Chemical: DPXE2Y45

PRZM environment: FLcabbageSTD.txt	modified Thuday, 24 May 2007 at
09:40:46

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w12842.dvf	modified Wedday, 3 July 2002 at 09:04:28

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	1.406	1.346	0.794	0.3003	0.2002	0.04937

1962	1.103	1.061	0.9077	0.6735	0.5705	0.2149

1963	4.089	3.965	3.353	2.267	1.514	0.4025

1964	1.649	1.604	1.496	1.222	1.049	0.4626

1965	0.8052	0.7746	0.6729	0.5195	0.4609	0.1914

1966	0.5683	0.5482	0.4899	0.396	0.3517	0.1329

1967	0.3716	0.3561	0.3007	0.2029	0.1662	0.07783

1968	1.63	1.562	1.349	1.076	0.8381	0.2815

1969	0.973	0.9404	0.8026	0.5369	0.4565	0.2743

1970	0.6234	0.6122	0.5464	0.4237	0.3588	0.136

1971	0.5694	0.5458	0.4667	0.3378	0.2813	0.168

1972	0.666	0.6424	0.5989	0.5563	0.4038	0.2127

1973	0.9073	0.8654	0.7319	0.6267	0.4291	0.2042

1974	0.8208	0.7894	0.5586	0.3239	0.273	0.1338

1975	1.146	1.095	0.9137	0.6472	0.4685	0.2292

1976	0.3185	0.3085	0.2717	0.2118	0.2065	0.1397

1977	0.4746	0.455	0.4334	0.2619	0.1778	0.1033

1978	1.011	0.9684	0.8195	0.5967	0.4321	0.1785

1979	0.6415	0.62	0.5852	0.4773	0.4112	0.1565

1980	0.6651	0.6391	0.5879	0.3732	0.2526	0.1222

1981	1.269	1.221	0.5794	0.4337	0.3664	0.171

1982	1.14	1.091	0.957	0.7298	0.6195	0.246

1983	0.8137	0.7921	0.6872	0.3459	0.2728	0.1638

1984	0.6459	0.624	0.5445	0.4169	0.3499	0.1241

1985	3.806	3.686	3.099	2.211	1.506	0.4164

1986	1.883	1.815	1.538	1.18	0.8552	0.4738

1987	1.437	1.377	1.199	0.9291	0.6282	0.3171

1988	2.431	2.324	1.962	1.237	0.8325	0.3431

1989	1.158	1.114	0.9571	0.7389	0.6214	0.3438

1990	0.5552	0.5357	0.4647	0.3606	0.3061	0.1114

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	4.089	3.965	3.353	2.267	1.514	0.4738

0.0645161290322581	3.806	3.686	3.099	2.211	1.506	0.4626

0.0967741935483871	2.431	2.324	1.962	1.237	1.049	0.4164

0.129032258064516	1.883	1.815	1.538	1.222	0.8552	0.4025

0.161290322580645	1.649	1.604	1.496	1.18	0.8381	0.3438

0.193548387096774	1.63	1.562	1.349	1.076	0.8325	0.3431

0.225806451612903	1.437	1.377	1.199	0.9291	0.6282	0.3171

0.258064516129032	1.406	1.346	0.9571	0.7389	0.6214	0.2815

0.290322580645161	1.269	1.221	0.957	0.7298	0.6195	0.2743

0.32258064516129	1.158	1.114	0.9137	0.6735	0.5705	0.246

0.354838709677419	1.146	1.095	0.9077	0.6472	0.4685	0.2292

0.387096774193548	1.14	1.091	0.8195	0.6267	0.4609	0.2149

0.419354838709677	1.103	1.061	0.8026	0.5967	0.4565	0.2127

0.451612903225806	1.011	0.9684	0.794	0.5563	0.4321	0.2042

0.483870967741936	0.973	0.9404	0.7319	0.5369	0.4291	0.1914

0.516129032258065	0.9073	0.8654	0.6872	0.5195	0.4112	0.1785

0.548387096774194	0.8208	0.7921	0.6729	0.4773	0.4038	0.171

0.580645161290323	0.8137	0.7894	0.5989	0.4337	0.3664	0.168

0.612903225806452	0.8052	0.7746	0.5879	0.4237	0.3588	0.1638

0.645161290322581	0.666	0.6424	0.5852	0.4169	0.3517	0.1565

0.67741935483871	0.6651	0.6391	0.5794	0.396	0.3499	0.1397

0.709677419354839	0.6459	0.624	0.5586	0.3732	0.3061	0.136

0.741935483870968	0.6415	0.62	0.5464	0.3606	0.2813	0.1338

0.774193548387097	0.6234	0.6122	0.5445	0.3459	0.273	0.1329

0.806451612903226	0.5694	0.5482	0.4899	0.3378	0.2728	0.1241

0.838709677419355	0.5683	0.5458	0.4667	0.3239	0.2526	0.1222

0.870967741935484	0.5552	0.5357	0.4647	0.3003	0.2065	0.1114

0.903225806451613	0.4746	0.455	0.4334	0.2619	0.2002	0.1033

0.935483870967742	0.3716	0.3561	0.3007	0.2118	0.1778	0.07783

0.967741935483871	0.3185	0.3085	0.2717	0.2029	0.1662	0.04937

0.1	2.3762	2.2731	1.9196	1.2355	1.02962	0.41501

					Average of yearly averages:	0.219396666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: FLCABAIR

Metfile:	w12842.dvf

PRZM scenario:	FLcabbageSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.0728	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.00	fraction of application rate applied to pond

Application Date	Date	16-10	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	3	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.0728	kg/ha

Interval 2	interval	3	days	Set to 0 or delete line for single app.

app. rate 2	apprate	0.0728	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

FL Cucumber

stored as FLCUCAIR.out

Chemical: DPXE2Y45

PRZM environment: FLcucumberSTD.txt	modified Wedday, 13 June 2007 at
11:19:24

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w12844.dvf	modified Wedday, 3 July 2002 at 09:04:30

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	1.517	1.453	1.234	0.8963	0.675	0.1664

1962	0.6598	0.6318	0.5354	0.3936	0.3154	0.1917

1963	1.463	1.301	1.115	0.9652	0.8055	0.3056

1964	2.791	2.679	2.283	2.102	1.495	0.6684

1965	6.679	6.463	5.489	4.004	2.978	1.012

1966	3.438	3.316	2.843	2.089	1.562	0.9159

1967	1.837	1.763	1.494	1.111	0.8135	0.4485

1968	1.451	1.394	1.223	1.023	0.7919	0.3331

1969	3.925	3.813	3.304	2.464	1.861	0.6751

1970	1.222	1.189	1.07	0.8671	0.7522	0.3022

1971	2.708	2.602	2.258	1.677	1.242	0.3716

1972	7.724	7.418	6.317	4.399	2.945	0.9258

1973	2.912	2.823	2.532	2.018	1.723	0.697

1974	1.308	1.254	1.078	0.7599	0.5774	0.3332

1975	0.7003	0.6717	0.5766	0.4722	0.3708	0.221

1976	2.445	2.352	2.015	1.54	1.066	0.3352

1977	1.978	1.923	1.669	1.024	0.6969	0.4209

1978	3.461	3.373	2.96	2.257	1.66	0.6134

1979	1.345	1.304	1.153	0.9004	0.763	0.4168

1980	0.6153	0.6008	0.5137	0.3992	0.3072	0.1843

1981	4.533	4.329	3.604	2.502	1.672	0.4782

1982	5.33	5.151	4.609	3.52	2.413	1.029

1983	3.433	3.3	3.093	2.391	1.773	0.8568

1984	4.673	4.487	3.844	2.759	1.911	0.7309

1985	2.124	2.046	1.763	1.329	1.118	0.4426

1986	2.754	2.7	2.473	2.017	1.539	0.6553

1987	5.299	5.107	4.496	3.293	2.208	0.7639

1988	1.896	1.85	1.658	1.314	1.119	0.5586

1989	0.9276	0.8912	0.7557	0.5475	0.4402	0.2263

1990	0.9959	0.9523	0.7972	0.5679	0.4213	0.2368

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	7.724	7.418	6.317	4.399	2.978	1.029

0.0645161290322581	6.679	6.463	5.489	4.004	2.945	1.012

0.0967741935483871	5.33	5.151	4.609	3.52	2.413	0.9258

0.129032258064516	5.299	5.107	4.496	3.293	2.208	0.9159

0.161290322580645	4.673	4.487	3.844	2.759	1.911	0.8568

0.193548387096774	4.533	4.329	3.604	2.502	1.861	0.7639

0.225806451612903	3.925	3.813	3.304	2.464	1.773	0.7309

0.258064516129032	3.461	3.373	3.093	2.391	1.723	0.697

0.290322580645161	3.438	3.316	2.96	2.257	1.672	0.6751

0.32258064516129	3.433	3.3	2.843	2.102	1.66	0.6684

0.354838709677419	2.912	2.823	2.532	2.089	1.562	0.6553

0.387096774193548	2.791	2.7	2.473	2.018	1.539	0.6134

0.419354838709677	2.754	2.679	2.283	2.017	1.495	0.5586

0.451612903225806	2.708	2.602	2.258	1.677	1.242	0.4782

0.483870967741936	2.445	2.352	2.015	1.54	1.119	0.4485

0.516129032258065	2.124	2.046	1.763	1.329	1.118	0.4426

0.548387096774194	1.978	1.923	1.669	1.314	1.066	0.4209

0.580645161290323	1.896	1.85	1.658	1.111	0.8135	0.4168

0.612903225806452	1.837	1.763	1.494	1.024	0.8055	0.3716

0.645161290322581	1.517	1.453	1.234	1.023	0.7919	0.3352

0.67741935483871	1.463	1.394	1.223	0.9652	0.763	0.3332

0.709677419354839	1.451	1.304	1.153	0.9004	0.7522	0.3331

0.741935483870968	1.345	1.301	1.115	0.8963	0.6969	0.3056

0.774193548387097	1.308	1.254	1.078	0.8671	0.675	0.3022

0.806451612903226	1.222	1.189	1.07	0.7599	0.5774	0.2368

0.838709677419355	0.9959	0.9523	0.7972	0.5679	0.4402	0.2263

0.870967741935484	0.9276	0.8912	0.7557	0.5475	0.4213	0.221

0.903225806451613	0.7003	0.6717	0.5766	0.4722	0.3708	0.1917

0.935483870967742	0.6598	0.6318	0.5354	0.3992	0.3154	0.1843

0.967741935483871	0.6153	0.6008	0.5137	0.3936	0.3072	0.1664

0.1	5.3269	5.1466	4.5977	3.4973	2.3925	0.92481

					Average of yearly averages:	0.517216666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: FLCUCAIR

Metfile:	w12844.dvf

PRZM scenario:	FLcucumberSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.0728	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.00	fraction of application rate applied to pond

Application Date	Date	16-10	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	3	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.0728	kg/ha

Interval 2	interval	3	days	Set to 0 or delete line for single app.

app. rate 2	apprate	0.0728	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

FL Pepper

stored as FLPEPAIR.out

Chemical: DPXE2Y45

PRZM environment: FLpeppersSTD.txt	modified Thuday, 24 May 2007 at
09:44:22

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w12844.dvf	modified Wedday, 3 July 2002 at 09:04:30

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.6543	0.6257	0.5531	0.5235	0.4612	0.1251

1962	4.186	4.013	3.525	2.553	2.091	0.5978

1963	2.668	2.6	2.429	1.976	1.655	0.6411

1964	4.561	4.428	4.015	3.17	2.633	0.8667

1965	4.396	4.21	3.653	2.679	2.126	0.764

1966	2.907	2.807	2.71	2.237	1.897	0.7983

1967	3.618	3.489	3.131	2.667	2.232	0.7462

1968	3.329	3.261	2.915	2.196	1.82	0.7151

1969	3.366	3.24	3.05	2.389	1.978	0.7275

1970	3.049	2.923	2.674	2.142	1.763	0.6403

1971	2.097	2.014	1.774	1.485	1.289	0.4942

1972	3.439	3.307	2.829	2.019	1.535	0.5526

1973	2.045	1.966	1.762	1.387	1.146	0.6024

1974	2.358	2.263	1.943	1.496	1.28	0.4585

1975	6.167	5.902	5.181	3.799	3.121	0.9581

1976	5.079	4.87	4.194	3.163	2.636	0.9701

1977	5.67	5.458	4.889	3.996	3.323	1.169

1978	1.534	1.475	1.274	0.9939	0.8523	0.5068

1979	8.24	7.909	6.92	5.088	4.175	1.247

1980	2.127	2.037	1.714	1.387	1.206	0.6656

1981	4.197	4.039	3.452	2.669	2.258	0.7205

1982	2.268	2.177	1.889	1.557	1.321	0.5354

1983	3.901	3.733	3.165	2.31	1.885	0.6264

1984	3.083	2.957	2.57	1.982	1.665	0.6098

1985	4.648	4.448	3.948	2.952	2.403	0.7849

1986	1.436	1.4	1.205	0.8905	0.791	0.4256

1987	3.608	3.457	3.039	2.447	2.044	0.6494

1988	1.98	1.89	1.569	1.271	1.045	0.4415

1989	1.456	1.395	1.251	1.131	0.9533	0.3651

1990	6.753	6.455	5.812	4.277	3.471	1.01

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	8.24	7.909	6.92	5.088	4.175	1.247

0.0645161290322581	6.753	6.455	5.812	4.277	3.471	1.169

0.0967741935483871	6.167	5.902	5.181	3.996	3.323	1.01

0.129032258064516	5.67	5.458	4.889	3.799	3.121	0.9701

0.161290322580645	5.079	4.87	4.194	3.17	2.636	0.9581

0.193548387096774	4.648	4.448	4.015	3.163	2.633	0.8667

0.225806451612903	4.561	4.428	3.948	2.952	2.403	0.7983

0.258064516129032	4.396	4.21	3.653	2.679	2.258	0.7849

0.290322580645161	4.197	4.039	3.525	2.669	2.232	0.764

0.32258064516129	4.186	4.013	3.452	2.667	2.126	0.7462

0.354838709677419	3.901	3.733	3.165	2.553	2.091	0.7275

0.387096774193548	3.618	3.489	3.131	2.447	2.044	0.7205

0.419354838709677	3.608	3.457	3.05	2.389	1.978	0.7151

0.451612903225806	3.439	3.307	3.039	2.31	1.897	0.6656

0.483870967741936	3.366	3.261	2.915	2.237	1.885	0.6494

0.516129032258065	3.329	3.24	2.829	2.196	1.82	0.6411

0.548387096774194	3.083	2.957	2.71	2.142	1.763	0.6403

0.580645161290323	3.049	2.923	2.674	2.019	1.665	0.6264

0.612903225806452	2.907	2.807	2.57	1.982	1.655	0.6098

0.645161290322581	2.668	2.6	2.429	1.976	1.535	0.6024

0.67741935483871	2.358	2.263	1.943	1.557	1.321	0.5978

0.709677419354839	2.268	2.177	1.889	1.496	1.289	0.5526

0.741935483870968	2.127	2.037	1.774	1.485	1.28	0.5354

0.774193548387097	2.097	2.014	1.762	1.387	1.206	0.5068

0.806451612903226	2.045	1.966	1.714	1.387	1.146	0.4942

0.838709677419355	1.98	1.89	1.569	1.271	1.045	0.4585

0.870967741935484	1.534	1.475	1.274	1.131	0.9533	0.4415

0.903225806451613	1.456	1.4	1.251	0.9939	0.8523	0.4256

0.935483870967742	1.436	1.395	1.205	0.8905	0.791	0.3651

0.967741935483871	0.6543	0.6257	0.5531	0.5235	0.4612	0.1251

0.1	6.1173	5.8576	5.1518	3.9763	3.3028	1.00601

					Average of yearly averages:	0.6805

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: FLPEPAIR

Metfile:	w12844.dvf

PRZM scenario:	FLpeppersSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1098	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.00	fraction of application rate applied to pond

Application Date	Date	1-9	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	5	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1098	kg/ha

Interval 2	interval	5	days	Set to 0 or delete line for single app.

app. rate 2	apprate	0.1098	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

FL Tomato

stored as FLTOMAIR.out

Chemical: DPXE2Y45

PRZM environment: FLtomatoSTD.txt	modified Tueday, 29 May 2007 at
12:54:10

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w12844.dvf	modified Wedday, 3 July 2002 at 09:04:30

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	1.34	1.284	1.193	0.9286	0.7714	0.2653

1962	1.385	1.328	1.156	0.8875	0.7384	0.2834

1963	0.6418	0.6211	0.5326	0.3918	0.3215	0.1527

1964	1.462	1.402	1.193	0.8842	0.7777	0.3116

1965	0.8418	0.8153	0.6958	0.5021	0.4115	0.1906

1966	4.481	4.305	3.675	2.758	2.264	0.7921

1967	1.568	1.506	1.275	1.108	0.9542	0.3914

1968	0.8068	0.7736	0.6537	0.4916	0.4115	0.1654

1969	1.35	1.301	1.141	0.8942	0.8079	0.3116

1970	2.389	2.298	2.126	1.653	1.362	0.5032

1971	0.8095	0.7798	0.6594	0.5006	0.4116	0.1546

1972	0.6599	0.6332	0.5533	0.4748	0.479	0.2003

1973	0.4381	0.4212	0.3605	0.331	0.3015	0.1318

1974	1.385	1.324	1.105	0.816	0.6802	0.2443

1975	0.3674	0.352	0.3125	0.2367	0.1954	0.07378

1976	2.325	2.235	1.994	1.46	1.198	0.4127

1977	1.554	1.489	1.366	1.095	0.8979	0.307

1978	0.3821	0.3677	0.3155	0.2675	0.2271	0.09268

1979	3.905	3.739	3.156	2.279	1.837	0.6014

1980	1.455	1.396	1.189	0.9139	0.7567	0.2739

1981	1.252	1.199	1.008	0.776	0.637	0.2313

1982	1.673	1.604	1.408	1.168	0.9823	0.3472

1983	1.548	1.487	1.381	1.067	0.8736	0.3052

1984	3.303	3.169	2.688	2.103	1.788	0.625

1985	1.977	1.89	1.583	1.346	1.142	0.4007

1986	1.078	1.034	0.941	0.7408	0.6191	0.2323

1987	1.827	1.754	1.622	1.229	1.003	0.3349

1988	0.6064	0.582	0.522	0.4274	0.383	0.152

1989	0.9712	0.9469	0.8093	0.5689	0.46	0.1786

1990	0.709	0.678	0.5695	0.4212	0.3555	0.1428

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	4.481	4.305	3.675	2.758	2.264	0.7921

0.0645161290322581	3.905	3.739	3.156	2.279	1.837	0.625

0.0967741935483871	3.303	3.169	2.688	2.103	1.788	0.6014

0.129032258064516	2.389	2.298	2.126	1.653	1.362	0.5032

0.161290322580645	2.325	2.235	1.994	1.46	1.198	0.4127

0.193548387096774	1.977	1.89	1.622	1.346	1.142	0.4007

0.225806451612903	1.827	1.754	1.583	1.229	1.003	0.3914

0.258064516129032	1.673	1.604	1.408	1.168	0.9823	0.3472

0.290322580645161	1.568	1.506	1.381	1.108	0.9542	0.3349

0.32258064516129	1.554	1.489	1.366	1.095	0.8979	0.3116

0.354838709677419	1.548	1.487	1.275	1.067	0.8736	0.3116

0.387096774193548	1.462	1.402	1.193	0.9286	0.8079	0.307

0.419354838709677	1.455	1.396	1.193	0.9139	0.7777	0.3052

0.451612903225806	1.385	1.328	1.189	0.8942	0.7714	0.2834

0.483870967741936	1.385	1.324	1.156	0.8875	0.7567	0.2739

0.516129032258065	1.35	1.301	1.141	0.8842	0.7384	0.2653

0.548387096774194	1.34	1.284	1.105	0.816	0.6802	0.2443

0.580645161290323	1.252	1.199	1.008	0.776	0.637	0.2323

0.612903225806452	1.078	1.034	0.941	0.7408	0.6191	0.2313

0.645161290322581	0.9712	0.9469	0.8093	0.5689	0.479	0.2003

0.67741935483871	0.8418	0.8153	0.6958	0.5021	0.46	0.1906

0.709677419354839	0.8095	0.7798	0.6594	0.5006	0.4116	0.1786

0.741935483870968	0.8068	0.7736	0.6537	0.4916	0.4115	0.1654

0.774193548387097	0.709	0.678	0.5695	0.4748	0.4115	0.1546

0.806451612903226	0.6599	0.6332	0.5533	0.4274	0.383	0.1527

0.838709677419355	0.6418	0.6211	0.5326	0.4212	0.3555	0.152

0.870967741935484	0.6064	0.582	0.522	0.3918	0.3215	0.1428

0.903225806451613	0.4381	0.4212	0.3605	0.331	0.3015	0.1318

0.935483870967742	0.3821	0.3677	0.3155	0.2675	0.2271	0.09268

0.967741935483871	0.3674	0.352	0.3125	0.2367	0.1954	0.07378

0.1	3.2116	3.0819	2.6318	2.058	1.7454	0.59158

					Average of yearly averages:	0.293658666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: FLTOMAIR

Metfile:	w12844.dvf

PRZM scenario:	FLtomatoSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1098	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.00	fraction of application rate applied to pond

Application Date	Date	1-2	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	5	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1098	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

GA Peach

stored as GAPEACHAIR.out

Chemical: DPXE2Y45

PRZM environment: GAPeachesSTD.txt	modified Tueday, 29 May 2007 at
12:54:56

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w03813.dvf	modified Wedday, 3 July 2002 at 09:04:32

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.02252	0.02161	0.01836	0.01356	0.01132	0.003818

1962	0.5092	0.4873	0.4138	0.3005	0.2447	0.07906

1963	0.2125	0.2037	0.1727	0.1258	0.1028	0.03971

1964	0.8193	0.7847	0.6606	0.4745	0.3892	0.1336

1965	0.03618	0.03553	0.03295	0.02825	0.02553	0.01487

1966	0.2178	0.2098	0.1845	0.1345	0.1095	0.03679

1967	0.1794	0.1726	0.1479	0.1099	0.09099	0.03649

1968	0.6628	0.6356	0.5384	0.3874	0.3162	0.1065

1969	0.03147	0.03108	0.02946	0.02592	0.02331	0.01046

1970	0.002935	0.002823	0.00242	0.001798	0.001506	0.0008568

1971	0.2938	0.2816	0.2376	0.1716	0.1414	0.04743

1972	0.03909	0.03802	0.03282	0.02404	0.01971	0.01021

1973	0.3161	0.3033	0.2578	0.1881	0.1538	0.05052

1974	0.2436	0.2337	0.1981	0.1438	0.1177	0.04251

1975	0.03607	0.03476	0.03	0.02545	0.02218	0.01069

1976	1.602	1.549	1.335	0.977	0.7964	0.2619

1977	0.07823	0.07709	0.0725	0.06214	0.05526	0.02336

1978	0.006156	0.00593	0.005112	0.003905	0.003437	0.001869

1979	0.07724	0.07419	0.06318	0.046	0.03779	0.01261

1980	0.003594	0.003547	0.003353	0.002922	0.002631	0.001275

1981	0.42	0.4014	0.3362	0.2388	0.1943	0.06218

1982	0.02312	0.02276	0.02134	0.01849	0.01662	0.008801

1983	0.179	0.1717	0.1462	0.1048	0.08421	0.02701

1984	0.3066	0.2935	0.2446	0.1734	0.141	0.0482

1985	0.01429	0.01406	0.01314	0.01137	0.01021	0.004433

1986	0.0005725	0.0005623	0.0005217	0.0004464	0.000398	0.0001657

1987	0.01027	0.00984	0.008309	0.007461	0.006378	0.002134

1988	0.007133	0.006827	0.005734	0.004126	0.003368	0.001212

1989	0.2571	0.2463	0.2078	0.1506	0.1261	0.04309

1990	0.01163	0.01144	0.01067	0.009172	0.008207	0.004517

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	1.602	1.549	1.335	0.977	0.7964	0.2619

0.0645161290322581	0.8193	0.7847	0.6606	0.4745	0.3892	0.1336

0.0967741935483871	0.6628	0.6356	0.5384	0.3874	0.3162	0.1065

0.129032258064516	0.5092	0.4873	0.4138	0.3005	0.2447	0.07906

0.161290322580645	0.42	0.4014	0.3362	0.2388	0.1943	0.06218

0.193548387096774	0.3161	0.3033	0.2578	0.1881	0.1538	0.05052

0.225806451612903	0.3066	0.2935	0.2446	0.1734	0.1414	0.0482

0.258064516129032	0.2938	0.2816	0.2376	0.1716	0.141	0.04743

0.290322580645161	0.2571	0.2463	0.2078	0.1506	0.1261	0.04309

0.32258064516129	0.2436	0.2337	0.1981	0.1438	0.1177	0.04251

0.354838709677419	0.2178	0.2098	0.1845	0.1345	0.1095	0.03971

0.387096774193548	0.2125	0.2037	0.1727	0.1258	0.1028	0.03679

0.419354838709677	0.1794	0.1726	0.1479	0.1099	0.09099	0.03649

0.451612903225806	0.179	0.1717	0.1462	0.1048	0.08421	0.02701

0.483870967741936	0.07823	0.07709	0.0725	0.06214	0.05526	0.02336

0.516129032258065	0.07724	0.07419	0.06318	0.046	0.03779	0.01487

0.548387096774194	0.03909	0.03802	0.03295	0.02825	0.02553	0.01261

0.580645161290323	0.03618	0.03553	0.03282	0.02592	0.02331	0.01069

0.612903225806452	0.03607	0.03476	0.03	0.02545	0.02218	0.01046

0.645161290322581	0.03147	0.03108	0.02946	0.02404	0.01971	0.01021

0.67741935483871	0.02312	0.02276	0.02134	0.01849	0.01662	0.008801

0.709677419354839	0.02252	0.02161	0.01836	0.01356	0.01132	0.004517

0.741935483870968	0.01429	0.01406	0.01314	0.01137	0.01021	0.004433

0.774193548387097	0.01163	0.01144	0.01067	0.009172	0.008207	0.003818

0.806451612903226	0.01027	0.00984	0.008309	0.007461	0.006378	0.002134

0.838709677419355	0.007133	0.006827	0.005734	0.004126	0.003437	0.001869

0.870967741935484	0.006156	0.00593	0.005112	0.003905	0.003368	0.001275

0.903225806451613	0.003594	0.003547	0.003353	0.002922	0.002631	0.001212

0.935483870967742	0.002935	0.002823	0.00242	0.001798	0.001506	0.0008568

0.967741935483871	0.0005725	0.0005623	0.0005217	0.0004464	0.000398
0.0001657

0.1	0.64744	0.62077	0.52594	0.37871	0.30905	0.103756

					Average of yearly averages:	0.0375423833333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: GAPEACHAIR

Metfile:	w03813.dvf

PRZM scenario:	GAPeachesSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1109	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.00	fraction of application rate applied to pond

Application Date	Date	1-5	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	7	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1109	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

ID Potato

stored as IDPOTAIR.out

Chemical: DPXE2Y45

PRZM environment: IDNpotato_WirrigSTD.txt	modified Tueday, 29 May 2007
at 12:55:22

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w24156.dvf	modified Wedday, 3 July 2002 at 09:04:38

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.2489	0.2399	0.207	0.1597	0.1332	0.047

1962	0.02675	0.02674	0.02669	0.02642	0.02522	0.01483

1963	0.4366	0.4231	0.3942	0.3268	0.2772	0.1054

1964	0.2516	0.2434	0.2134	0.1708	0.1487	0.07011

1965	0.03431	0.03324	0.03059	0.02738	0.02595	0.01762

1966	0.1075	0.1034	0.08842	0.07783	0.07168	0.02899

1967	0.2465	0.2379	0.2066	0.172	0.1502	0.05835

1968	0.1702	0.1643	0.147	0.1269	0.1076	0.04618

1969	0.2758	0.2661	0.2347	0.1879	0.156	0.06241

1970	0.7912	0.7629	0.6633	0.5171	0.4292	0.1577

1971	0.5256	0.5112	0.4522	0.348	0.2919	0.1291

1972	0.3606	0.3516	0.3077	0.2333	0.1986	0.08671

1973	0.131	0.1261	0.1126	0.0876	0.07293	0.03681

1974	0.7437	0.7176	0.6202	0.4636	0.4282	0.1753

1975	0.2482	0.2401	0.2106	0.1632	0.1381	0.07373

1976	0.7897	0.7627	0.6638	0.4944	0.4116	0.1505

1977	0.3285	0.3182	0.283	0.2242	0.1888	0.08505

1978	0.3748	0.362	0.3144	0.2349	0.1934	0.07609

1979	0.04437	0.04437	0.04436	0.04423	0.042	0.02444

1980	0.1061	0.1039	0.0962	0.07757	0.06473	0.02551

1981	0.4213	0.4077	0.3608	0.2708	0.2259	0.08883

1982	0.2168	0.2095	0.1832	0.1477	0.1369	0.0692

1983	0.1678	0.1621	0.1482	0.1277	0.1109	0.05075

1984	0.5217	0.5044	0.4402	0.3401	0.2932	0.1133

1985	0.3955	0.3806	0.3269	0.2506	0.213	0.09303

1986	0.1327	0.1286	0.118	0.1066	0.09446	0.04437

1987	0.1677	0.1617	0.1437	0.1116	0.09382	0.03634

1988	0.0302	0.02956	0.02819	0.02236	0.01864	0.01153

1989	0.03252	0.0318	0.03019	0.0268	0.02316	0.009865

1990	0.1084	0.1042	0.08992	0.07226	0.06059	0.02267

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	0.7912	0.7629	0.6638	0.5171	0.4292	0.1753

0.0645161290322581	0.7897	0.7627	0.6633	0.4944	0.4282	0.1577

0.0967741935483871	0.7437	0.7176	0.6202	0.4636	0.4116	0.1505

0.129032258064516	0.5256	0.5112	0.4522	0.348	0.2932	0.1291

0.161290322580645	0.5217	0.5044	0.4402	0.3401	0.2919	0.1133

0.193548387096774	0.4366	0.4231	0.3942	0.3268	0.2772	0.1054

0.225806451612903	0.4213	0.4077	0.3608	0.2708	0.2259	0.09303

0.258064516129032	0.3955	0.3806	0.3269	0.2506	0.213	0.08883

0.290322580645161	0.3748	0.362	0.3144	0.2349	0.1986	0.08671

0.32258064516129	0.3606	0.3516	0.3077	0.2333	0.1934	0.08505

0.354838709677419	0.3285	0.3182	0.283	0.2242	0.1888	0.07609

0.387096774193548	0.2758	0.2661	0.2347	0.1879	0.156	0.07373

0.419354838709677	0.2516	0.2434	0.2134	0.172	0.1502	0.07011

0.451612903225806	0.2489	0.2401	0.2106	0.1708	0.1487	0.0692

0.483870967741936	0.2482	0.2399	0.207	0.1632	0.1381	0.06241

0.516129032258065	0.2465	0.2379	0.2066	0.1597	0.1369	0.05835

0.548387096774194	0.2168	0.2095	0.1832	0.1477	0.1332	0.05075

0.580645161290323	0.1702	0.1643	0.1482	0.1277	0.1109	0.047

0.612903225806452	0.1678	0.1621	0.147	0.1269	0.1076	0.04618

0.645161290322581	0.1677	0.1617	0.1437	0.1116	0.09446	0.04437

0.67741935483871	0.1327	0.1286	0.118	0.1066	0.09382	0.03681

0.709677419354839	0.131	0.1261	0.1126	0.0876	0.07293	0.03634

0.741935483870968	0.1084	0.1042	0.0962	0.07783	0.07168	0.02899

0.774193548387097	0.1075	0.1039	0.08992	0.07757	0.06473	0.02551

0.806451612903226	0.1061	0.1034	0.08842	0.07226	0.06059	0.02444

0.838709677419355	0.04437	0.04437	0.04436	0.04423	0.042	0.02267

0.870967741935484	0.03431	0.03324	0.03059	0.02738	0.02595	0.01762

0.903225806451613	0.03252	0.0318	0.03019	0.0268	0.02522	0.01483

0.935483870967742	0.0302	0.02956	0.02819	0.02642	0.02316	0.01153

0.967741935483871	0.02675	0.02674	0.02669	0.02236	0.01864	0.009865

0.1	0.72189	0.69696	0.6034	0.45204	0.39976	0.14836

					Average of yearly averages:	0.0670571666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: IDPOTAIR

Metfile:	w24156.dvf

PRZM scenario:	IDNpotato_WirrigSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.0739	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.00	fraction of application rate applied to pond

Application Date	Date	1-4	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	3	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.0739	kg/ha

Interval 2	interval	3	days	Set to 0 or delete line for single app.

app. rate 2	apprate	0.0739	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

ME Potato

stored as MEPOTAIR.out

Chemical: DPXE2Y45

PRZM environment: MEpotatoSTD.txt	modified Tueday, 29 May 2007 at
12:56:18

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w14607.dvf	modified Wedday, 3 July 2002 at 09:05:36

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.6326	0.6151	0.553	0.5172	0.4721	0.1818

1962	1.201	1.167	1.089	0.9068	0.8224	0.4979

1963	0.7287	0.7108	0.6893	0.6381	0.6327	0.5198

1964	0.6345	0.6318	0.5914	0.5664	0.5048	0.4077

1965	0.6265	0.624	0.6145	0.5978	0.5886	0.3958

1966	0.6411	0.6253	0.5661	0.517	0.4522	0.2879

1967	0.7453	0.7254	0.6707	0.6251	0.5909	0.4619

1968	0.8265	0.8225	0.8073	0.7425	0.6512	0.5029

1969	0.9986	0.9724	0.8765	0.761	0.7523	0.6326

1970	1.271	1.235	1.108	0.9079	0.8273	0.5586

1971	0.6565	0.656	0.6539	0.6511	0.6498	0.4277

1972	0.9642	0.939	0.8534	0.7571	0.705	0.4899

1973	1.076	1.045	0.94	0.7777	0.6898	0.5376

1974	0.5972	0.5953	0.5878	0.5759	0.5751	0.4146

1975	0.4996	0.4871	0.4413	0.3833	0.3685	0.3001

1976	1.313	1.278	1.15	1.08	1.007	0.5891

1977	1.134	1.105	1.04	0.8991	0.8337	0.6515

1978	0.997	0.9726	0.8928	0.7317	0.6555	0.4883

1979	0.6894	0.6699	0.6259	0.5179	0.471	0.3925

1980	0.5623	0.5481	0.4984	0.4227	0.3939	0.3342

1981	2.152	2.081	1.834	1.462	1.296	0.6495

1982	1.076	1.046	0.9852	0.9057	0.8992	0.7255

1983	1.125	1.095	0.9821	0.9226	0.8439	0.5942

1984	0.9831	0.9605	0.8881	0.8154	0.7351	0.5277

1985	0.4016	0.3904	0.3638	0.3324	0.3275	0.2644

1986	0.774	0.7522	0.6763	0.6074	0.5576	0.3661

1987	0.4946	0.4925	0.4678	0.4322	0.4279	0.3681

1988	0.4614	0.4498	0.424	0.4036	0.4009	0.3261

1989	1.117	1.094	0.97	0.7867	0.6878	0.3926

1990	1.142	1.115	1.038	0.9899	0.9198	0.6626

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	2.152	2.081	1.834	1.462	1.296	0.7255

0.0645161290322581	1.313	1.278	1.15	1.08	1.007	0.6626

0.0967741935483871	1.271	1.235	1.108	0.9899	0.9198	0.6515

0.129032258064516	1.201	1.167	1.089	0.9226	0.8992	0.6495

0.161290322580645	1.142	1.115	1.04	0.9079	0.8439	0.6326

0.193548387096774	1.134	1.105	1.038	0.9068	0.8337	0.5942

0.225806451612903	1.125	1.095	0.9852	0.9057	0.8273	0.5891

0.258064516129032	1.117	1.094	0.9821	0.8991	0.8224	0.5586

0.290322580645161	1.076	1.046	0.97	0.8154	0.7523	0.5376

0.32258064516129	1.076	1.045	0.94	0.7867	0.7351	0.5277

0.354838709677419	0.9986	0.9726	0.8928	0.7777	0.705	0.5198

0.387096774193548	0.997	0.9724	0.8881	0.761	0.6898	0.5029

0.419354838709677	0.9831	0.9605	0.8765	0.7571	0.6878	0.4979

0.451612903225806	0.9642	0.939	0.8534	0.7425	0.6555	0.4899

0.483870967741936	0.8265	0.8225	0.8073	0.7317	0.6512	0.4883

0.516129032258065	0.774	0.7522	0.6893	0.6511	0.6498	0.4619

0.548387096774194	0.7453	0.7254	0.6763	0.6381	0.6327	0.4277

0.580645161290323	0.7287	0.7108	0.6707	0.6251	0.5909	0.4146

0.612903225806452	0.6894	0.6699	0.6539	0.6074	0.5886	0.4077

0.645161290322581	0.6565	0.656	0.6259	0.5978	0.5751	0.3958

0.67741935483871	0.6411	0.6318	0.6145	0.5759	0.5576	0.3926

0.709677419354839	0.6345	0.6253	0.5914	0.5664	0.5048	0.3925

0.741935483870968	0.6326	0.624	0.5878	0.5179	0.4721	0.3681

0.774193548387097	0.6265	0.6151	0.5661	0.5172	0.471	0.3661

0.806451612903226	0.5972	0.5953	0.553	0.517	0.4522	0.3342

0.838709677419355	0.5623	0.5481	0.4984	0.4322	0.4279	0.3261

0.870967741935484	0.4996	0.4925	0.4678	0.4227	0.4009	0.3001

0.903225806451613	0.4946	0.4871	0.4413	0.4036	0.3939	0.2879

0.935483870967742	0.4614	0.4498	0.424	0.3833	0.3685	0.2644

0.967741935483871	0.4016	0.3904	0.3638	0.3324	0.3275	0.1818

0.1	1.264	1.2282	1.1061	0.98317	0.91774	0.6513

					Average of yearly averages:	0.464973333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: MEPOTAIR

Metfile:	w14607.dvf

PRZM scenario:	MEpotatoSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.0739	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.00	fraction of application rate applied to pond

Application Date	Date	1-6	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	5	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.0739	kg/ha

Interval 2	interval	5	days	Set to 0 or delete line for single app.

app. rate 2	apprate	0.0739	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

MI Cherry

stored as MICHEAIR.out

Chemical: DPXE2Y45

PRZM environment: MICherriesSTD.txt	modified Tueday, 29 May 2007 at
12:56:56

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w14850.dvf	modified Wedday, 3 July 2002 at 09:05:40

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.1207	0.1167	0.1036	0.08319	0.07244	0.02514

1962	0.3802	0.3669	0.3197	0.2475	0.2112	0.09509

1963	0.9877	0.9578	0.8474	0.6579	0.5577	0.2332

1964	0.2901	0.2804	0.2448	0.2085	0.1829	0.1282

1965	0.1284	0.1254	0.1161	0.1047	0.1002	0.07545

1966	0.2056	0.1993	0.1752	0.1529	0.1391	0.0788

1967	0.1744	0.1696	0.1558	0.1452	0.1323	0.09175

1968	0.1238	0.1197	0.1048	0.09173	0.08106	0.04785

1969	0.6966	0.6747	0.6152	0.5291	0.4482	0.1725

1970	0.2086	0.203	0.1817	0.1656	0.148	0.1127

1971	0.125	0.121	0.1069	0.1005	0.1	0.07095

1972	0.2863	0.2768	0.2588	0.2086	0.1817	0.09549

1973	0.1131	0.1096	0.0994	0.08397	0.08023	0.06214

1974	0.3312	0.3213	0.2819	0.2277	0.1966	0.09479

1975	0.2823	0.274	0.2515	0.2041	0.1757	0.09614

1976	0.1366	0.1319	0.1149	0.09806	0.0941	0.06592

1977	0.1734	0.1682	0.151	0.1316	0.1183	0.06979

1978	0.5265	0.5088	0.4475	0.3563	0.3067	0.1495

1979	0.2534	0.2464	0.2207	0.1903	0.1828	0.1308

1980	0.19	0.184	0.1622	0.1265	0.109	0.07802

1981	0.4332	0.4187	0.3834	0.3282	0.3205	0.1492

1982	0.7982	0.7748	0.6776	0.5205	0.4449	0.2128

1983	0.3774	0.3675	0.3455	0.3024	0.2983	0.1934

1984	0.1507	0.1464	0.1312	0.122	0.1217	0.09616

1985	0.6627	0.6385	0.5535	0.4775	0.4297	0.1764

1986	1.033	1.01	0.9453	0.7532	0.6448	0.3176

1987	0.751	0.7274	0.6444	0.5313	0.4681	0.2604

1988	0.2425	0.2425	0.2424	0.2421	0.2417	0.1464

1989	0.6121	0.5922	0.5184	0.4183	0.3626	0.1599

1990	0.3184	0.3085	0.2879	0.2304	0.2011	0.1149

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	1.033	1.01	0.9453	0.7532	0.6448	0.3176

0.0645161290322581	0.9877	0.9578	0.8474	0.6579	0.5577	0.2604

0.0967741935483871	0.7982	0.7748	0.6776	0.5313	0.4681	0.2332

0.129032258064516	0.751	0.7274	0.6444	0.5291	0.4482	0.2128

0.161290322580645	0.6966	0.6747	0.6152	0.5205	0.4449	0.1934

0.193548387096774	0.6627	0.6385	0.5535	0.4775	0.4297	0.1764

0.225806451612903	0.6121	0.5922	0.5184	0.4183	0.3626	0.1725

0.258064516129032	0.5265	0.5088	0.4475	0.3563	0.3205	0.1599

0.290322580645161	0.4332	0.4187	0.3834	0.3282	0.3067	0.1495

0.32258064516129	0.3802	0.3675	0.3455	0.3024	0.2983	0.1492

0.354838709677419	0.3774	0.3669	0.3197	0.2475	0.2417	0.1464

0.387096774193548	0.3312	0.3213	0.2879	0.2421	0.2112	0.1308

0.419354838709677	0.3184	0.3085	0.2819	0.2304	0.2011	0.1282

0.451612903225806	0.2901	0.2804	0.2588	0.2277	0.1966	0.1149

0.483870967741936	0.2863	0.2768	0.2515	0.2086	0.1829	0.1127

0.516129032258065	0.2823	0.274	0.2448	0.2085	0.1828	0.09616

0.548387096774194	0.2534	0.2464	0.2424	0.2041	0.1817	0.09614

0.580645161290323	0.2425	0.2425	0.2207	0.1903	0.1757	0.09549

0.612903225806452	0.2086	0.203	0.1817	0.1656	0.148	0.09509

0.645161290322581	0.2056	0.1993	0.1752	0.1529	0.1391	0.09479

0.67741935483871	0.19	0.184	0.1622	0.1452	0.1323	0.09175

0.709677419354839	0.1744	0.1696	0.1558	0.1316	0.1217	0.0788

0.741935483870968	0.1734	0.1682	0.151	0.1265	0.1183	0.07802

0.774193548387097	0.1507	0.1464	0.1312	0.122	0.109	0.07545

0.806451612903226	0.1366	0.1319	0.1161	0.1047	0.1002	0.07095

0.838709677419355	0.1284	0.1254	0.1149	0.1005	0.1	0.06979

0.870967741935484	0.125	0.121	0.1069	0.09806	0.0941	0.06592

0.903225806451613	0.1238	0.1197	0.1048	0.09173	0.08106	0.06214

0.935483870967742	0.1207	0.1167	0.1036	0.08397	0.08023	0.04785

0.967741935483871	0.1131	0.1096	0.0994	0.08319	0.07244	0.02514

0.1	0.79348	0.77006	0.67428	0.53108	0.46611	0.23116

					Average of yearly averages:	0.126712666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: MICHEAIR

Metfile:	w14850.dvf

PRZM scenario:	MICherriesSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1109	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.00	fraction of application rate applied to pond

Application Date	Date	1-5	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	7	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1109	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

MS Cotton

stored as MSCOTAIR.out

Chemical: DPXE2Y45

PRZM environment: MScottonSTD.txt	modified Tueday, 29 May 2007 at
12:57:52

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w03940.dvf	modified Wedday, 3 July 2002 at 09:05:46

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	1.472	1.411	1.192	0.9872	0.8817	0.3144

1962	0.2865	0.2755	0.2575	0.2034	0.1975	0.1118

1963	2.079	1.997	1.702	1.289	1.103	0.4056

1964	0.5399	0.5226	0.4757	0.428	0.3885	0.1824

1965	0.1581	0.1526	0.1332	0.1068	0.1004	0.06473

1966	3.353	3.295	2.935	2.139	1.743	0.5837

1967	2.984	2.866	2.516	2.105	1.813	0.6914

1968	1.76	1.691	1.615	1.249	1.033	0.3916

1969	0.2519	0.2438	0.225	0.2035	0.1929	0.1113

1970	0.5862	0.5704	0.4906	0.421	0.3763	0.1598

1971	2.581	2.475	2.106	1.559	1.281	0.4411

1972	1.541	1.489	1.337	1.07	0.9112	0.3444

1973	1.572	1.508	1.348	1.091	0.9081	0.3334

1974	1.135	1.088	0.9187	0.6644	0.556	0.2289

1975	2.407	2.319	2.17	1.718	1.44	0.5158

1976	3.641	3.503	3.229	2.595	2.196	0.778

1977	0.9365	0.9051	0.8052	0.6773	0.6399	0.295

1978	3.048	2.935	2.751	2.127	1.748	0.6135

1979	2.647	2.541	2.162	1.964	1.825	0.7129

1980	2.135	2.061	1.887	1.394	1.143	0.4411

1981	1.869	1.795	1.669	1.297	1.074	0.3788

1982	2.794	2.677	2.294	1.796	1.484	0.5082

1983	5.026	4.862	4.199	3.213	2.649	0.9204

1984	1.131	1.086	0.9877	0.9084	0.8064	0.3501

1985	0.4351	0.4186	0.3818	0.3327	0.3077	0.1346

1986	2.195	2.11	1.858	1.396	1.159	0.3982

1987	1.174	1.13	1.002	0.8294	0.7743	0.3145

1988	0.6382	0.6131	0.5313	0.4528	0.4187	0.1846

1989	3.347	3.227	2.822	2.327	2.042	0.7556

1990	2.531	2.436	2.173	1.704	1.407	0.5146

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	5.026	4.862	4.199	3.213	2.649	0.9204

0.0645161290322581	3.641	3.503	3.229	2.595	2.196	0.778

0.0967741935483871	3.353	3.295	2.935	2.327	2.042	0.7556

0.129032258064516	3.347	3.227	2.822	2.139	1.825	0.7129

0.161290322580645	3.048	2.935	2.751	2.127	1.813	0.6914

0.193548387096774	2.984	2.866	2.516	2.105	1.748	0.6135

0.225806451612903	2.794	2.677	2.294	1.964	1.743	0.5837

0.258064516129032	2.647	2.541	2.173	1.796	1.484	0.5158

0.290322580645161	2.581	2.475	2.17	1.718	1.44	0.5146

0.32258064516129	2.531	2.436	2.162	1.704	1.407	0.5082

0.354838709677419	2.407	2.319	2.106	1.559	1.281	0.4411

0.387096774193548	2.195	2.11	1.887	1.396	1.159	0.4411

0.419354838709677	2.135	2.061	1.858	1.394	1.143	0.4056

0.451612903225806	2.079	1.997	1.702	1.297	1.103	0.3982

0.483870967741936	1.869	1.795	1.669	1.289	1.074	0.3916

0.516129032258065	1.76	1.691	1.615	1.249	1.033	0.3788

0.548387096774194	1.572	1.508	1.348	1.091	0.9112	0.3501

0.580645161290323	1.541	1.489	1.337	1.07	0.9081	0.3444

0.612903225806452	1.472	1.411	1.192	0.9872	0.8817	0.3334

0.645161290322581	1.174	1.13	1.002	0.9084	0.8064	0.3145

0.67741935483871	1.135	1.088	0.9877	0.8294	0.7743	0.3144

0.709677419354839	1.131	1.086	0.9187	0.6773	0.6399	0.295

0.741935483870968	0.9365	0.9051	0.8052	0.6644	0.556	0.2289

0.774193548387097	0.6382	0.6131	0.5313	0.4528	0.4187	0.1846

0.806451612903226	0.5862	0.5704	0.4906	0.428	0.3885	0.1824

0.838709677419355	0.5399	0.5226	0.4757	0.421	0.3763	0.1598

0.870967741935484	0.4351	0.4186	0.3818	0.3327	0.3077	0.1346

0.903225806451613	0.2865	0.2755	0.2575	0.2035	0.1975	0.1118

0.935483870967742	0.2519	0.2438	0.225	0.2034	0.1929	0.1113

0.967741935483871	0.1581	0.1526	0.1332	0.1068	0.1004	0.06473

0.1	3.3524	3.2882	2.9237	2.3082	2.0203	0.75133

					Average of yearly averages:	0.406014333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: MSCOTAIR

Metfile:	w03940.dvf

PRZM scenario:	MScottonSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1109	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.00	fraction of application rate applied to pond

Application Date	Date	1-5	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	5	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1109	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

NC Apple

stored as NCAPPAIR.out

Chemical: DPXE2Y45

PRZM environment: NCappleSTD.txt	modified Tueday, 29 May 2007 at
12:58:16

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w03812.dvf	modified Wedday, 3 July 2002 at 09:05:50

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1965	0.2081	0.2004	0.174	0.1488	0.1318	0.04861

1966	0.3098	0.2987	0.2602	0.201	0.1674	0.06324

1967	0.2056	0.1983	0.1796	0.1541	0.1317	0.05144

1968	0.0924	0.08905	0.08136	0.06371	0.05563	0.02621

1969	0.5727	0.5508	0.471	0.3602	0.2998	0.1064

1970	0.2395	0.2339	0.2022	0.1508	0.1264	0.05254

1971	0.184	0.1772	0.1567	0.1243	0.1052	0.04228

1972	0.6106	0.5885	0.5275	0.3974	0.3287	0.1177

1973	1.439	1.387	1.223	0.9348	0.7808	0.2906

1974	0.7027	0.6758	0.6273	0.57	0.5009	0.2033

1975	0.6573	0.6381	0.5715	0.4371	0.3647	0.1372

1976	0.4772	0.4618	0.4051	0.3355	0.2833	0.1075

1977	0.6581	0.6333	0.5435	0.4317	0.3636	0.1375

1978	0.2884	0.2774	0.2614	0.2035	0.1689	0.06728

1979	0.7969	0.7666	0.6924	0.5499	0.4719	0.1767

1980	1.019	0.9871	0.8442	0.6712	0.5661	0.2064

1981	0.08236	0.07965	0.07188	0.06298	0.05382	0.02985

1982	0.2079	0.2	0.1747	0.1362	0.1145	0.04261

1983	0.6179	0.5959	0.5324	0.4714	0.406	0.1472

1984	0.3829	0.3691	0.3248	0.2608	0.2322	0.09522

1985	0.1878	0.1804	0.1537	0.1156	0.09904	0.04376

1986	0.1736	0.1672	0.1459	0.1075	0.08837	0.0326

1987	0.4314	0.4149	0.3552	0.3048	0.2886	0.1121

1988	0.4593	0.4415	0.3774	0.2769	0.2269	0.09005

1989	0.2706	0.2604	0.2253	0.1715	0.145	0.05667

1990	0.3391	0.3267	0.289	0.2256	0.1876	0.07031

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.037037037037037	1.439	1.387	1.223	0.9348	0.7808	0.2906

0.0740740740740741	1.019	0.9871	0.8442	0.6712	0.5661	0.2064

0.111111111111111	0.7969	0.7666	0.6924	0.57	0.5009	0.2033

0.148148148148148	0.7027	0.6758	0.6273	0.5499	0.4719	0.1767

0.185185185185185	0.6581	0.6381	0.5715	0.4714	0.406	0.1472

0.222222222222222	0.6573	0.6333	0.5435	0.4371	0.3647	0.1375

0.259259259259259	0.6179	0.5959	0.5324	0.4317	0.3636	0.1372

0.296296296296296	0.6106	0.5885	0.5275	0.3974	0.3287	0.1177

0.333333333333333	0.5727	0.5508	0.471	0.3602	0.2998	0.1121

0.37037037037037	0.4772	0.4618	0.4051	0.3355	0.2886	0.1075

0.407407407407407	0.4593	0.4415	0.3774	0.3048	0.2833	0.1064

0.444444444444444	0.4314	0.4149	0.3552	0.2769	0.2322	0.09522

0.481481481481481	0.3829	0.3691	0.3248	0.2608	0.2269	0.09005

0.518518518518518	0.3391	0.3267	0.289	0.2256	0.1876	0.07031

0.555555555555556	0.3098	0.2987	0.2614	0.2035	0.1689	0.06728

0.592592592592593	0.2884	0.2774	0.2602	0.201	0.1674	0.06324

0.62962962962963	0.2706	0.2604	0.2253	0.1715	0.145	0.05667

0.666666666666667	0.2395	0.2339	0.2022	0.1541	0.1318	0.05254

0.703703703703704	0.2081	0.2004	0.1796	0.1508	0.1317	0.05144

0.740740740740741	0.2079	0.2	0.1747	0.1488	0.1264	0.04861

0.777777777777778	0.2056	0.1983	0.174	0.1362	0.1145	0.04376

0.814814814814815	0.1878	0.1804	0.1567	0.1243	0.1052	0.04261

0.851851851851852	0.184	0.1772	0.1537	0.1156	0.09904	0.04228

0.888888888888889	0.1736	0.1672	0.1459	0.1075	0.08837	0.0326

0.925925925925926	0.0924	0.08905	0.08136	0.06371	0.05563	0.02985

0.962962962962963	0.08236	0.07965	0.07188	0.06298	0.05382	0.02621

0.1	0.86353	0.83275	0.73794	0.60036	0.52046	0.20423

					Average of yearly averages:	0.0982796153846154

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: NCAPPAIR

Metfile:	w03812.dvf

PRZM scenario:	NCappleSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1109	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.00	fraction of application rate applied to pond

Application Date	Date	1-4	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	10	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1109	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

NC Cotton

stored as NCCOTAIR.out

Chemical: DPXE2Y45

PRZM environment: NCcottonSTD.txt	modified Tueday, 29 May 2007 at
12:58:38

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w13722.dvf	modified Wedday, 3 July 2002 at 09:05:50

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.7135	0.6934	0.6327	0.5246	0.4925	0.2002

1962	2.02	1.95	1.84	1.539	1.378	0.5803

1963	1.164	1.121	0.9622	0.7417	0.5719	0.2872

1964	1.261	1.216	1.085	1.04	0.9243	0.5209

1965	4.19	4.045	3.588	3.094	2.668	1.033

1966	1.68	1.624	1.446	1.229	1.189	0.6223

1967	2.975	2.879	2.678	2.29	2.088	0.8591

1968	1.249	1.219	1.065	0.8683	0.7832	0.4749

1969	1.466	1.417	1.311	1.091	1.026	0.5336

1970	1.339	1.292	1.2	1.145	1.021	0.4578

1971	1.083	1.051	0.922	0.8903	0.8568	0.448

1972	2.036	1.992	1.8	1.765	1.629	0.6948

1973	3.854	3.714	3.215	2.608	2.228	0.8639

1974	1.045	1.011	0.8885	0.7825	0.6863	0.3935

1975	2.132	2.055	1.785	1.338	1.187	0.5172

1976	1.481	1.425	1.224	1.065	0.9436	0.4082

1977	1.576	1.517	1.333	1.122	1.035	0.5277

1978	1.494	1.441	1.25	1.068	0.9838	0.5358

1979	1.406	1.364	1.237	1.105	1.103	0.5712

1980	2.184	2.098	1.795	1.338	1.178	0.5477

1981	1.76	1.696	1.474	1.35	1.265	0.5703

1982	3.269	3.169	2.808	2.274	1.96	0.8478

1983	0.6457	0.6255	0.5717	0.5346	0.4732	0.3403

1984	1.894	1.826	1.684	1.311	1.104	0.5025

1985	1.222	1.193	1.046	0.9194	0.8519	0.4324

1986	2.009	1.939	1.749	1.363	1.175	0.5107

1987	1.593	1.535	1.382	1.122	0.9431	0.4507

1988	1.03	0.994	0.9227	0.7782	0.7012	0.3615

1989	1.081	1.045	0.9813	0.9215	0.8873	0.4376

1990	0.8048	0.7737	0.6763	0.5171	0.4287	0.2047

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	4.19	4.045	3.588	3.094	2.668	1.033

0.0645161290322581	3.854	3.714	3.215	2.608	2.228	0.8639

0.0967741935483871	3.269	3.169	2.808	2.29	2.088	0.8591

0.129032258064516	2.975	2.879	2.678	2.274	1.96	0.8478

0.161290322580645	2.184	2.098	1.84	1.765	1.629	0.6948

0.193548387096774	2.132	2.055	1.8	1.539	1.378	0.6223

0.225806451612903	2.036	1.992	1.795	1.363	1.265	0.5803

0.258064516129032	2.02	1.95	1.785	1.35	1.189	0.5712

0.290322580645161	2.009	1.939	1.749	1.338	1.187	0.5703

0.32258064516129	1.894	1.826	1.684	1.338	1.178	0.5477

0.354838709677419	1.76	1.696	1.474	1.311	1.175	0.5358

0.387096774193548	1.68	1.624	1.446	1.229	1.104	0.5336

0.419354838709677	1.593	1.535	1.382	1.145	1.103	0.5277

0.451612903225806	1.576	1.517	1.333	1.122	1.035	0.5209

0.483870967741936	1.494	1.441	1.311	1.122	1.026	0.5172

0.516129032258065	1.481	1.425	1.25	1.105	1.021	0.5107

0.548387096774194	1.466	1.417	1.237	1.091	0.9838	0.5025

0.580645161290323	1.406	1.364	1.224	1.068	0.9436	0.4749

0.612903225806452	1.339	1.292	1.2	1.065	0.9431	0.4578

0.645161290322581	1.261	1.219	1.085	1.04	0.9243	0.4507

0.67741935483871	1.249	1.216	1.065	0.9215	0.8873	0.448

0.709677419354839	1.222	1.193	1.046	0.9194	0.8568	0.4376

0.741935483870968	1.164	1.121	0.9813	0.8903	0.8519	0.4324

0.774193548387097	1.083	1.051	0.9622	0.8683	0.7832	0.4082

0.806451612903226	1.081	1.045	0.9227	0.7825	0.7012	0.3935

0.838709677419355	1.045	1.011	0.922	0.7782	0.6863	0.3615

0.870967741935484	1.03	0.994	0.8885	0.7417	0.5719	0.3403

0.903225806451613	0.8048	0.7737	0.6763	0.5346	0.4925	0.2872

0.935483870967742	0.7135	0.6934	0.6327	0.5246	0.4732	0.2047

0.967741935483871	0.6457	0.6255	0.5717	0.5171	0.4287	0.2002

0.1	3.2396	3.14	2.795	2.2884	2.0752	0.85797

					Average of yearly averages:	0.524526666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: NCCOTAIR

Metfile:	w13722.dvf

PRZM scenario:	NCcottonSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1109	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.00	fraction of application rate applied to pond

Application Date	Date	1-6	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	5	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1109	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

NY Grape

stored as CACOTAIR.out

Chemical: DPXE2Y45

PRZM environment: NYGrapesSTD.txt	modified Tueday, 29 May 2007 at
12:59:44

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w14860.dvf	modified Wedday, 3 July 2002 at 09:06:14

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.1127	0.1099	0.0995	0.08593	0.08161	0.04125

1962	1.107	1.075	0.9791	0.8028	0.7724	0.3429

1963	0.3513	0.3513	0.3512	0.3496	0.3343	0.202

1964	0.7512	0.7257	0.6324	0.4844	0.4113	0.2081

1965	0.4647	0.4487	0.3903	0.3102	0.2742	0.1818

1966	0.4894	0.4748	0.4212	0.3531	0.3448	0.1923

1967	1.09	1.055	0.9393	0.7441	0.644	0.2896

1968	0.2481	0.248	0.2472	0.2433	0.2338	0.1319

1969	0.147	0.1432	0.1289	0.1061	0.09827	0.07231

1970	0.7079	0.6842	0.6383	0.5018	0.4529	0.1922

1971	0.4809	0.4658	0.4095	0.3341	0.2994	0.2029

1972	0.8107	0.7877	0.7301	0.611	0.5291	0.2556

1973	0.8589	0.8368	0.7537	0.6201	0.5574	0.2885

1974	0.7993	0.7786	0.6817	0.5402	0.4839	0.2714

1975	0.6302	0.6115	0.5633	0.4563	0.415	0.2765

1976	0.4286	0.4202	0.3749	0.3211	0.2831	0.1855

1977	0.5302	0.5227	0.491	0.4267	0.397	0.2001

1978	0.4496	0.4349	0.4033	0.366	0.3424	0.2013

1979	0.7436	0.7196	0.6346	0.5594	0.5463	0.3021

1980	1.038	1.01	0.9045	0.8181	0.7545	0.4415

1981	0.3785	0.3785	0.3784	0.3765	0.3595	0.2498

1982	0.7478	0.7297	0.66	0.5534	0.4973	0.2519

1983	0.8111	0.7855	0.7384	0.6374	0.5913	0.2979

1984	0.7624	0.7417	0.6735	0.5429	0.4918	0.299

1985	0.6575	0.6397	0.5904	0.539	0.4901	0.2772

1986	1.313	1.278	1.153	0.9386	0.8146	0.4498

1987	0.4808	0.4666	0.4163	0.3771	0.354	0.2751

1988	0.2952	0.2852	0.2571	0.2329	0.2229	0.1451

1989	0.5858	0.5744	0.5132	0.4043	0.3677	0.2033

1990	0.5559	0.5397	0.509	0.4268	0.3682	0.1747

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	1.313	1.278	1.153	0.9386	0.8146	0.4498

0.0645161290322581	1.107	1.075	0.9791	0.8181	0.7724	0.4415

0.0967741935483871	1.09	1.055	0.9393	0.8028	0.7545	0.3429

0.129032258064516	1.038	1.01	0.9045	0.7441	0.644	0.3021

0.161290322580645	0.8589	0.8368	0.7537	0.6374	0.5913	0.299

0.193548387096774	0.8111	0.7877	0.7384	0.6201	0.5574	0.2979

0.225806451612903	0.8107	0.7855	0.7301	0.611	0.5463	0.2896

0.258064516129032	0.7993	0.7786	0.6817	0.5594	0.5291	0.2885

0.290322580645161	0.7624	0.7417	0.6735	0.5534	0.4973	0.2772

0.32258064516129	0.7512	0.7297	0.66	0.5429	0.4918	0.2765

0.354838709677419	0.7478	0.7257	0.6383	0.5402	0.4901	0.2751

0.387096774193548	0.7436	0.7196	0.6346	0.539	0.4839	0.2714

0.419354838709677	0.7079	0.6842	0.6324	0.5018	0.4529	0.2556

0.451612903225806	0.6575	0.6397	0.5904	0.4844	0.415	0.2519

0.483870967741936	0.6302	0.6115	0.5633	0.4563	0.4113	0.2498

0.516129032258065	0.5858	0.5744	0.5132	0.4268	0.397	0.2081

0.548387096774194	0.5559	0.5397	0.509	0.4267	0.3682	0.2033

0.580645161290323	0.5302	0.5227	0.491	0.4043	0.3677	0.2029

0.612903225806452	0.4894	0.4748	0.4212	0.3771	0.3595	0.202

0.645161290322581	0.4809	0.4666	0.4163	0.3765	0.354	0.2013

0.67741935483871	0.4808	0.4658	0.4095	0.366	0.3448	0.2001

0.709677419354839	0.4647	0.4487	0.4033	0.3531	0.3424	0.1923

0.741935483870968	0.4496	0.4349	0.3903	0.3496	0.3343	0.1922

0.774193548387097	0.4286	0.4202	0.3784	0.3341	0.2994	0.1855

0.806451612903226	0.3785	0.3785	0.3749	0.3211	0.2831	0.1818

0.838709677419355	0.3513	0.3513	0.3512	0.3102	0.2742	0.1747

0.870967741935484	0.2952	0.2852	0.2571	0.2433	0.2338	0.1451

0.903225806451613	0.2481	0.248	0.2472	0.2329	0.2229	0.1319

0.935483870967742	0.147	0.1432	0.1289	0.1061	0.09827	0.07231

0.967741935483871	0.1127	0.1099	0.0995	0.08593	0.08161	0.04125

0.1	1.0848	1.0505	0.93582	0.79693	0.74345	0.33882

					Average of yearly averages:	0.236785333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CACOTAIR

Metfile:	w14860.dvf

PRZM scenario:	NYGrapesSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1109	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.00	fraction of application rate applied to pond

Application Date	Date	1-6	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	7	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1109	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

OR Apple

stored as ORAPPAIR.out

Chemical: DPXE2Y45

PRZM environment: ORappleSTD.txt	modified Tueday, 29 May 2007 at
13:00:08

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w24232.dvf	modified Wedday, 3 July 2002 at 09:06:10

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.1129	0.1093	0.09623	0.07413	0.0618	0.02641

1962	0.2064	0.2	0.1803	0.1428	0.1203	0.06342

1963	0.6386	0.6169	0.5388	0.4182	0.3558	0.1587

1964	0.1877	0.1837	0.1727	0.1422	0.09891	0.05555

1965	0.1922	0.1887	0.1699	0.1382	0.09932	0.0742

1966	0.2665	0.261	0.241	0.1874	0.1289	0.06426

1967	0.1752	0.1716	0.1579	0.1326	0.1176	0.06874

1968	0.1393	0.1365	0.1205	0.1069	0.0988	0.06174

1969	0.1716	0.1663	0.1497	0.1341	0.1239	0.06761

1970	0.08218	0.08094	0.07607	0.06588	0.05905	0.03831

1971	0.4962	0.484	0.4288	0.3336	0.2889	0.1473

1972	0.1925	0.1881	0.1659	0.1294	0.116	0.07748

1973	0.09086	0.08898	0.08191	0.06903	0.0615	0.03898

1974	0.3876	0.3791	0.3457	0.2856	0.1926	0.06125

1975	0.239	0.2341	0.2155	0.1824	0.1622	0.09506

1976	0.0578	0.05677	0.0528	0.04525	0.04059	0.01932

1977	0.05346	0.05185	0.0466	0.04221	0.0355	0.02082

1978	0.2865	0.2771	0.2424	0.1865	0.1564	0.06864

1979	0.1225	0.1192	0.1113	0.09337	0.08866	0.05732

1980	0.2015	0.1954	0.1859	0.156	0.146	0.08357

1981	0.2638	0.2565	0.2326	0.1862	0.1943	0.1217

1982	0.2185	0.2118	0.1884	0.1475	0.1258	0.07054

1983	0.06966	0.06762	0.06007	0.04864	0.04533	0.03658

1984	0.2788	0.2703	0.2389	0.2074	0.1939	0.09042

1985	0.2519	0.2427	0.2117	0.157	0.1297	0.07448

1986	0.09607	0.09452	0.08818	0.07632	0.06865	0.04415

1987	0.2519	0.2479	0.2324	0.1461	0.1141	0.07518

1988	0.1892	0.1851	0.1696	0.1412	0.1242	0.07808

1989	0.2766	0.2691	0.2415	0.1908	0.1395	0.04855

1990	0.1942	0.19	0.181	0.1527	0.1349	0.08173

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	0.6386	0.6169	0.5388	0.4182	0.3558	0.1587

0.0645161290322581	0.4962	0.484	0.4288	0.3336	0.2889	0.1473

0.0967741935483871	0.3876	0.3791	0.3457	0.2856	0.1943	0.1217

0.129032258064516	0.2865	0.2771	0.2424	0.2074	0.1939	0.09506

0.161290322580645	0.2788	0.2703	0.2415	0.1908	0.1926	0.09042

0.193548387096774	0.2766	0.2691	0.241	0.1874	0.1622	0.08357

0.225806451612903	0.2665	0.261	0.2389	0.1865	0.1564	0.08173

0.258064516129032	0.2638	0.2565	0.2326	0.1862	0.146	0.07808

0.290322580645161	0.2519	0.2479	0.2324	0.1824	0.1395	0.07748

0.32258064516129	0.2519	0.2427	0.2155	0.157	0.1349	0.07518

0.354838709677419	0.239	0.2341	0.2117	0.156	0.1297	0.07448

0.387096774193548	0.2185	0.2118	0.1884	0.1527	0.1289	0.0742

0.419354838709677	0.2064	0.2	0.1859	0.1475	0.1258	0.07054

0.451612903225806	0.2015	0.1954	0.181	0.1461	0.1242	0.06874

0.483870967741936	0.1942	0.19	0.1803	0.1428	0.1239	0.06864

0.516129032258065	0.1925	0.1887	0.1727	0.1422	0.1203	0.06761

0.548387096774194	0.1922	0.1881	0.1699	0.1412	0.1176	0.06426

0.580645161290323	0.1892	0.1851	0.1696	0.1382	0.116	0.06342

0.612903225806452	0.1877	0.1837	0.1659	0.1341	0.1141	0.06174

0.645161290322581	0.1752	0.1716	0.1579	0.1326	0.09932	0.06125

0.67741935483871	0.1716	0.1663	0.1497	0.1294	0.09891	0.05732

0.709677419354839	0.1393	0.1365	0.1205	0.1069	0.0988	0.05555

0.741935483870968	0.1225	0.1192	0.1113	0.09337	0.08866	0.04855

0.774193548387097	0.1129	0.1093	0.09623	0.07632	0.06865	0.04415

0.806451612903226	0.09607	0.09452	0.08818	0.07413	0.0618	0.03898

0.838709677419355	0.09086	0.08898	0.08191	0.06903	0.0615	0.03831

0.870967741935484	0.08218	0.08094	0.07607	0.06588	0.05905	0.03658

0.903225806451613	0.06966	0.06762	0.06007	0.04864	0.04533	0.02641

0.935483870967742	0.0578	0.05677	0.0528	0.04525	0.04059	0.02082

0.967741935483871	0.05346	0.05185	0.0466	0.04221	0.0355	0.01932

0.1	0.37749	0.3689	0.33537	0.27778	0.19426	0.119036

					Average of yearly averages:	0.069003

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: ORAPPAIR

Metfile:	w24232.dvf

PRZM scenario:	ORappleSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1109	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.00	fraction of application rate applied to pond

Application Date	Date	1-4	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	10	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1109	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

PA Apple

stored as PAPPAIR.out

Chemical: DPXE2Y45

PRZM environment: PAappleSTD.txt	modified Tueday, 29 May 2007 at
13:01:58

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w14751.dvf	modified Wedday, 3 July 2002 at 09:06:14

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.3221	0.3099	0.2757	0.2129	0.1775	0.05886

1962	0.1307	0.1261	0.1095	0.08491	0.07772	0.0502

1963	0.04857	0.04698	0.04114	0.03639	0.03556	0.02413

1964	0.2324	0.224	0.1939	0.1595	0.1537	0.06824

1965	0.07541	0.07271	0.06291	0.05594	0.05353	0.03254

1966	0.6936	0.6687	0.5808	0.439	0.3695	0.1234

1967	0.2708	0.2627	0.2329	0.186	0.1749	0.1204

1968	0.9133	0.8929	0.779	0.5845	0.4844	0.1943

1969	0.5522	0.5332	0.4771	0.3574	0.2967	0.1303

1970	0.1558	0.1508	0.1445	0.1236	0.107	0.07525

1971	0.2402	0.2321	0.2022	0.156	0.1336	0.05939

1972	0.5067	0.4905	0.4302	0.3304	0.2815	0.1277

1973	0.4286	0.4154	0.3631	0.2803	0.2444	0.112

1974	0.5059	0.488	0.4283	0.3447	0.3032	0.1265

1975	0.5669	0.5478	0.4973	0.416	0.3659	0.1528

1976	0.3311	0.3196	0.2832	0.2431	0.2095	0.09189

1977	0.1225	0.1186	0.1037	0.08133	0.08112	0.05039

1978	0.4506	0.4351	0.3899	0.307	0.2642	0.1033

1979	0.2977	0.2877	0.2561	0.218	0.1937	0.08521

1980	0.5649	0.545	0.4735	0.3827	0.3245	0.1292

1981	0.105	0.1014	0.09138	0.08226	0.07255	0.04548

1982	0.9582	0.9281	0.8308	0.6536	0.5447	0.1952

1983	0.6342	0.6134	0.5354	0.4441	0.3952	0.1662

1984	0.6129	0.5926	0.5215	0.4217	0.3564	0.148

1985	0.9379	0.9058	0.8043	0.6917	0.5958	0.2389

1986	0.6098	0.5899	0.522	0.4441	0.386	0.2027

1987	0.2976	0.2872	0.2486	0.1968	0.1804	0.09592

1988	0.2202	0.2129	0.1892	0.1514	0.132	0.06161

1989	1.212	1.172	1.119	0.8809	0.7435	0.2755

1990	0.774	0.7493	0.652	0.5099	0.4545	0.2

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	1.212	1.172	1.119	0.8809	0.7435	0.2755

0.0645161290322581	0.9582	0.9281	0.8308	0.6917	0.5958	0.2389

0.0967741935483871	0.9379	0.9058	0.8043	0.6536	0.5447	0.2027

0.129032258064516	0.9133	0.8929	0.779	0.5845	0.4844	0.2

0.161290322580645	0.774	0.7493	0.652	0.5099	0.4545	0.1952

0.193548387096774	0.6936	0.6687	0.5808	0.4441	0.3952	0.1943

0.225806451612903	0.6342	0.6134	0.5354	0.4441	0.386	0.1662

0.258064516129032	0.6129	0.5926	0.522	0.439	0.3695	0.1528

0.290322580645161	0.6098	0.5899	0.5215	0.4217	0.3659	0.148

0.32258064516129	0.5669	0.5478	0.4973	0.416	0.3564	0.1303

0.354838709677419	0.5649	0.545	0.4771	0.3827	0.3245	0.1292

0.387096774193548	0.5522	0.5332	0.4735	0.3574	0.3032	0.1277

0.419354838709677	0.5067	0.4905	0.4302	0.3447	0.2967	0.1265

0.451612903225806	0.5059	0.488	0.4283	0.3304	0.2815	0.1234

0.483870967741936	0.4506	0.4351	0.3899	0.307	0.2642	0.1204

0.516129032258065	0.4286	0.4154	0.3631	0.2803	0.2444	0.112

0.548387096774194	0.3311	0.3196	0.2832	0.2431	0.2095	0.1033

0.580645161290323	0.3221	0.3099	0.2757	0.218	0.1937	0.09592

0.612903225806452	0.2977	0.2877	0.2561	0.2129	0.1804	0.09189

0.645161290322581	0.2976	0.2872	0.2486	0.1968	0.1775	0.08521

0.67741935483871	0.2708	0.2627	0.2329	0.186	0.1749	0.07525

0.709677419354839	0.2402	0.2321	0.2022	0.1595	0.1537	0.06824

0.741935483870968	0.2324	0.224	0.1939	0.156	0.1336	0.06161

0.774193548387097	0.2202	0.2129	0.1892	0.1514	0.132	0.05939

0.806451612903226	0.1558	0.1508	0.1445	0.1236	0.107	0.05886

0.838709677419355	0.1307	0.1261	0.1095	0.08491	0.08112	0.05039

0.870967741935484	0.1225	0.1186	0.1037	0.08226	0.07772	0.0502

0.903225806451613	0.105	0.1014	0.09138	0.08133	0.07255	0.04548

0.935483870967742	0.07541	0.07271	0.06291	0.05594	0.05353	0.03254

0.967741935483871	0.04857	0.04698	0.04114	0.03639	0.03556	0.02413

0.1	0.93544	0.90451	0.80177	0.64669	0.53867	0.20243

					Average of yearly averages:	0.118183666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: PAPPAIR

Metfile:	w14751.dvf

PRZM scenario:	PAappleSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1109	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.00	fraction of application rate applied to pond

Application Date	Date	16-4	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	10	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1109	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

PA  Tomato

stored as PATOMAIR.out

Chemical: DPXE2Y45

PRZM environment: PAtomatoSTD.txt	modified Tueday, 29 May 2007 at
13:01:58

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w14751.dvf	modified Wedday, 3 July 2002 at 09:06:14

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	0.3387	0.3262	0.2903	0.2246	0.1879	0.07126

1962	0.2203	0.2127	0.1849	0.1441	0.131	0.07737

1963	0.06939	0.06701	0.0583	0.05445	0.0539	0.03698

1964	0.3337	0.3217	0.2782	0.2242	0.215	0.09527

1965	0.1537	0.1481	0.1291	0.1129	0.1046	0.05836

1966	0.6018	0.5806	0.5061	0.3848	0.3257	0.1342

1967	0.347	0.3361	0.2982	0.2342	0.213	0.1302

1968	1.063	1.043	0.9163	0.7009	0.6416	0.2617

1969	0.6447	0.6228	0.557	0.419	0.3485	0.1634

1970	0.1928	0.1873	0.1771	0.1524	0.138	0.09624

1971	0.2926	0.2838	0.2495	0.1978	0.1699	0.07712

1972	0.4915	0.4763	0.42	0.3252	0.3081	0.1408

1973	0.505	0.4899	0.4298	0.3604	0.3279	0.1415

1974	0.6952	0.6707	0.6022	0.4879	0.4282	0.1764

1975	0.8918	0.8621	0.7739	0.6464	0.5634	0.2257

1976	0.4947	0.4777	0.4325	0.3698	0.3172	0.1371

1977	0.3373	0.3254	0.2817	0.213	0.1916	0.09462

1978	0.6168	0.5958	0.5306	0.4217	0.3658	0.1473

1979	0.4338	0.4204	0.3792	0.3231	0.2871	0.1254

1980	0.6847	0.6609	0.589	0.4707	0.4068	0.1635

1981	0.1132	0.1095	0.09931	0.09108	0.08059	0.05421

1982	1.189	1.155	1.051	0.8292	0.693	0.252

1983	1.064	1.03	0.9014	0.8148	0.7008	0.2779

1984	0.5632	0.5449	0.4848	0.4007	0.3404	0.157

1985	1.169	1.13	1.003	0.8602	0.7437	0.2956

1986	0.8014	0.7757	0.6867	0.5895	0.5143	0.2689

1987	0.4373	0.4223	0.3661	0.2957	0.2703	0.1431

1988	0.3254	0.3145	0.2807	0.2262	0.1973	0.09186

1989	1.66	1.606	1.546	1.232	1.043	0.3895

1990	0.9391	0.9095	0.7926	0.6298	0.5652	0.2563

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	1.66	1.606	1.546	1.232	1.043	0.3895

0.0645161290322581	1.189	1.155	1.051	0.8602	0.7437	0.2956

0.0967741935483871	1.169	1.13	1.003	0.8292	0.7008	0.2779

0.129032258064516	1.064	1.043	0.9163	0.8148	0.693	0.2689

0.161290322580645	1.063	1.03	0.9014	0.7009	0.6416	0.2617

0.193548387096774	0.9391	0.9095	0.7926	0.6464	0.5652	0.2563

0.225806451612903	0.8918	0.8621	0.7739	0.6298	0.5634	0.252

0.258064516129032	0.8014	0.7757	0.6867	0.5895	0.5143	0.2257

0.290322580645161	0.6952	0.6707	0.6022	0.4879	0.4282	0.1764

0.32258064516129	0.6847	0.6609	0.589	0.4707	0.4068	0.1635

0.354838709677419	0.6447	0.6228	0.557	0.4217	0.3658	0.1634

0.387096774193548	0.6168	0.5958	0.5306	0.419	0.3485	0.157

0.419354838709677	0.6018	0.5806	0.5061	0.4007	0.3404	0.1473

0.451612903225806	0.5632	0.5449	0.4848	0.3848	0.3279	0.1431

0.483870967741936	0.505	0.4899	0.4325	0.3698	0.3257	0.1415

0.516129032258065	0.4947	0.4777	0.4298	0.3604	0.3172	0.1408

0.548387096774194	0.4915	0.4763	0.42	0.3252	0.3081	0.1371

0.580645161290323	0.4373	0.4223	0.3792	0.3231	0.2871	0.1342

0.612903225806452	0.4338	0.4204	0.3661	0.2957	0.2703	0.1302

0.645161290322581	0.347	0.3361	0.2982	0.2342	0.215	0.1254

0.67741935483871	0.3387	0.3262	0.2903	0.2262	0.213	0.09624

0.709677419354839	0.3373	0.3254	0.2817	0.2246	0.1973	0.09527

0.741935483870968	0.3337	0.3217	0.2807	0.2242	0.1916	0.09462

0.774193548387097	0.3254	0.3145	0.2782	0.213	0.1879	0.09186

0.806451612903226	0.2926	0.2838	0.2495	0.1978	0.1699	0.07737

0.838709677419355	0.2203	0.2127	0.1849	0.1524	0.138	0.07712

0.870967741935484	0.1928	0.1873	0.1771	0.1441	0.131	0.07126

0.903225806451613	0.1537	0.1481	0.1291	0.1129	0.1046	0.05836

0.935483870967742	0.1132	0.1095	0.09931	0.09108	0.08059	0.05421

0.967741935483871	0.06939	0.06701	0.0583	0.05445	0.0539	0.03698

0.1	1.1585	1.1213	0.99433	0.82776	0.70002	0.277

					Average of yearly averages:	0.158026333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: PATOMAIR

Metfile:	w14751.dvf

PRZM scenario:	PAtomatoSTD.txt

EXAMS environment file:	pond298.exv

Chemical Name:	DPXE2Y45

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	483.15	g/mol

Henry's Law Const.	henry	3.1E-15	atm-m^3/mol

Vapor Pressure	vapr	1.57E-13	torr

Solubility	sol	1.023	mg/L

Kd	Kd		mg/L

Koc	Koc	328	mg/L

Photolysis half-life	kdp	0.31	days	Half-life

Aerobic Aquatic Metabolism	kbacw	341.1355	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	208	days	Halfife

Aerobic Soil Metabolism	asm	631.76	days	Halfife

Hydrolysis:	pH 7		days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI		cm

Application Rate:	TAPP	0.1098	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.00	fraction of application rate applied to pond

Application Date	Date	16-4	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	5	days	Set to 0 or delete line for single app.

app. rate 1	apprate	0.1098	kg/ha

Record 17:	FILTRA	

	IPSCND	

	UPTKF	

Record 18:	PLVKRT	

	PLDKRT	0.019804

	FEXTRC	0.5

Flag for Index Res. Run	IR	EPA Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)



APPENDIX C

Initial Federally Listed Species

	Species Counts by State for Indicated Crops

	No species were excluded.

	Minimum of 1 Acre.

	All Medium Types Reported

	broccoli, brussels sprouts, cabbage - head, cauliflower, celery,
chinese 

	cabbage, collards, escarole and endive, kale, lettuce, all, lettuce,
head, 

	lettuce, leaf, lettuce, romaine, mustard cabbage (bok choy), mustard
greens 

	(mizuna), parsley, rhubarb, spinach, turnip greens, watercress,
cantaloups, 

	cucumbers and pickles, honeydew melons, pumpkins, squash, watermelons, 

	eggplant, okra, peppers, bell, peppers, chile (all peppers - excluding
bell), 

	pimientos, tomatoes, cotton, all, apples, pears, all, pears, bartlett
(AZ, CA, 

	ID, OR, & WA only), pears, other (AZ, CA, ID, OR, & WA only), potatoes,


	almonds, apricots, cherries, sweet, cherries, tart, nectarines,
peaches, all, 

	peaches, clingstone (AZ & CA only), peaches, freestone (AZ & CA only), 

	plums (AZ & CA only), plums and prunes, prunes (AZ & CA only), grapes

	AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS, KY,
LA, ME, MD, MA, MI, 

	MN, MS, MO, MT, NE, NV, NH, NJ, NM, NY, NC, ND, OH, OK, OR, PA, PR, RI,
SC, SD, TN, 

	TX, UT, VT, VA, WA, WV, WI, WY

	Alabama

	The taxa Amphibian has 2 species co-occurring with indicated crops.

	The taxa Bird has 3 species co-occurring with indicated crops.

	The taxa Bivalve has 30 species co-occurring with indicated crops.

	The taxa Crustacean has 1 species co-occurring with indicated crops.

	The taxa Dicot has 10 species co-occurring with indicated crops.

	The taxa Ferns has 3 species co-occurring with indicated crops.

	The taxa Fish has 15 species co-occurring with indicated crops.

	The taxa Gastropod has 10 species co-occurring with indicated crops.

	The taxa Mammal has 4 species co-occurring with indicated crops.

	The taxa Monocot has 3 species co-occurring with indicated crops.

	The taxa Reptile has 8 species co-occurring with indicated crops.

	Alaska

	The taxa Ferns has 1 species co-occurring with indicated crops.

	The taxa Reptile has 1 species co-occurring with indicated crops.

	Arizona

12/4/2007 10:34:09 AM   Ver. 2.10.3	Page 1 of 15

	AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS,
KY, LA, ME, MD, MA, MI, 

	MN, MS, MO, MT, NE, NV, NH, NJ, NM, NY, NC, ND, OH, OK, OR, PA, PR, RI,
SC, SD, TN, 

	TX, UT, VT, VA, WA, WV, WI, WY

	The taxa Amphibian has 2 species co-occurring with indicated crops.

	The taxa Bird has 7 species co-occurring with indicated crops.

	The taxa Dicot has 16 species co-occurring with indicated crops.

	The taxa Fish has 18 species co-occurring with indicated crops.

	The taxa Gastropod has 1 species co-occurring with indicated crops.

	The taxa Mammal has 9 species co-occurring with indicated crops.

	The taxa Monocot has 2 species co-occurring with indicated crops.

	The taxa Reptile has 2 species co-occurring with indicated crops.

	Arkansas

	The taxa Bird has 2 species co-occurring with indicated crops.

	The taxa Bivalve has 6 species co-occurring with indicated crops.

	The taxa Crustacean has 2 species co-occurring with indicated crops.

	The taxa Dicot has 4 species co-occurring with indicated crops.

	The taxa Fish has 3 species co-occurring with indicated crops.

	The taxa Gastropod has 1 species co-occurring with indicated crops.

	The taxa Insect has 1 species co-occurring with indicated crops.

	The taxa Mammal has 3 species co-occurring with indicated crops.

	California

	The taxa Amphibian has 6 species co-occurring with indicated crops.

	The taxa Bird has 15 species co-occurring with indicated crops.

	The taxa Conf/cycds has 2 species co-occurring with indicated crops.

	The taxa Crustacean has 9 species co-occurring with indicated crops.

	The taxa Dicot has 159 species co-occurring with indicated crops.

	The taxa Fish has 31 species co-occurring with indicated crops.

	The taxa Gastropod has 1 species co-occurring with indicated crops.

	The taxa Insect has 22 species co-occurring with indicated crops.

	The taxa Mammal has 20 species co-occurring with indicated crops.

	The taxa Monocot has 17 species co-occurring with indicated crops.

	The taxa Reptile has 11 species co-occurring with indicated crops.

12/4/2007 10:34:09 AM   Ver. 2.10.3	Page 2 of 15

	AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS,
KY, LA, ME, MD, MA, MI, 

	MN, MS, MO, MT, NE, NV, NH, NJ, NM, NY, NC, ND, OH, OK, OR, PA, PR, RI,
SC, SD, TN, 

	TX, UT, VT, VA, WA, WV, WI, WY

	Colorado

	The taxa Bird has 2 species co-occurring with indicated crops.

	The taxa Dicot has 10 species co-occurring with indicated crops.

	The taxa Fish has 6 species co-occurring with indicated crops.

	The taxa Insect has 2 species co-occurring with indicated crops.

	The taxa Mammal has 2 species co-occurring with indicated crops.

	The taxa Monocot has 1 species co-occurring with indicated crops.

	Connecticut

	The taxa Bird has 2 species co-occurring with indicated crops.

	The taxa Bivalve has 1 species co-occurring with indicated crops.

	The taxa Dicot has 1 species co-occurring with indicated crops.

	The taxa Fish has 1 species co-occurring with indicated crops.

	The taxa Insect has 1 species co-occurring with indicated crops.

	The taxa Mammal has 1 species co-occurring with indicated crops.

	The taxa Monocot has 1 species co-occurring with indicated crops.

	The taxa Reptile has 6 species co-occurring with indicated crops.

	Delaware

	The taxa Bird has 1 species co-occurring with indicated crops.

	The taxa Fish has 1 species co-occurring with indicated crops.

	The taxa Mammal has 1 species co-occurring with indicated crops.

	The taxa Monocot has 2 species co-occurring with indicated crops.

	The taxa Reptile has 6 species co-occurring with indicated crops.

	Florida

	The taxa Amphibian has 1 species co-occurring with indicated crops.

	The taxa Bird has 8 species co-occurring with indicated crops.

	The taxa Bivalve has 7 species co-occurring with indicated crops.

	The taxa Conf/cycds has 1 species co-occurring with indicated crops.

	The taxa Crustacean has 1 species co-occurring with indicated crops.

	The taxa Dicot has 46 species co-occurring with indicated crops.

12/4/2007 10:34:09 AM   Ver. 2.10.3	Page 3 of 15

	AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS,
KY, LA, ME, MD, MA, MI, 

	MN, MS, MO, MT, NE, NV, NH, NJ, NM, NY, NC, ND, OH, OK, OR, PA, PR, RI,
SC, SD, TN, 

	TX, UT, VT, VA, WA, WV, WI, WY

	The taxa Fish has 4 species co-occurring with indicated crops.

	The taxa Insect has 1 species co-occurring with indicated crops.

	The taxa Mammal has 8 species co-occurring with indicated crops.

	The taxa Monocot has 2 species co-occurring with indicated crops.

	The taxa Reptile has 10 species co-occurring with indicated crops.

	Georgia

	The taxa Amphibian has 1 species co-occurring with indicated crops.

	The taxa Bird has 4 species co-occurring with indicated crops.

	The taxa Bivalve has 16 species co-occurring with indicated crops.

	The taxa Conf/cycds has 1 species co-occurring with indicated crops.

	The taxa Dicot has 10 species co-occurring with indicated crops.

	The taxa Ferns has 2 species co-occurring with indicated crops.

	The taxa Fish has 11 species co-occurring with indicated crops.

	The taxa Insect has 1 species co-occurring with indicated crops.

	The taxa Mammal has 3 species co-occurring with indicated crops.

	The taxa Monocot has 6 species co-occurring with indicated crops.

	The taxa Reptile has 6 species co-occurring with indicated crops.

	Hawaii

	The taxa Arachnid has 1 species co-occurring with indicated crops.

	The taxa Bird has 32 species co-occurring with indicated crops.

	The taxa Crustacean has 1 species co-occurring with indicated crops.

	The taxa Dicot has 233 species co-occurring with indicated crops.

	The taxa Ferns has 12 species co-occurring with indicated crops.

	The taxa Gastropod has 39 species co-occurring with indicated crops.

	The taxa Insect has 1 species co-occurring with indicated crops.

	The taxa Mammal has 1 species co-occurring with indicated crops.

	The taxa Monocot has 22 species co-occurring with indicated crops.

	The taxa Reptile has 4 species co-occurring with indicated crops.

	Idaho

12/4/2007 10:34:09 AM   Ver. 2.10.3	Page 4 of 15

	AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS,
KY, LA, ME, MD, MA, MI, 

	MN, MS, MO, MT, NE, NV, NH, NJ, NM, NY, NC, ND, OH, OK, OR, PA, PR, RI,
SC, SD, TN, 

	TX, UT, VT, VA, WA, WV, WI, WY

	The taxa Bird has 1 species co-occurring with indicated crops.

	The taxa Dicot has 3 species co-occurring with indicated crops.

	The taxa Fish has 8 species co-occurring with indicated crops.

	The taxa Gastropod has 6 species co-occurring with indicated crops.

	The taxa Mammal has 4 species co-occurring with indicated crops.

	Illinois

	The taxa Bird has 2 species co-occurring with indicated crops.

	The taxa Bivalve has 7 species co-occurring with indicated crops.

	The taxa Crustacean has 1 species co-occurring with indicated crops.

	The taxa Dicot has 7 species co-occurring with indicated crops.

	The taxa Fish has 1 species co-occurring with indicated crops.

	The taxa Gastropod has 1 species co-occurring with indicated crops.

	The taxa Insect has 2 species co-occurring with indicated crops.

	The taxa Mammal has 2 species co-occurring with indicated crops.

	The taxa Monocot has 2 species co-occurring with indicated crops.

	Indiana

	The taxa Bird has 2 species co-occurring with indicated crops.

	The taxa Bivalve has 11 species co-occurring with indicated crops.

	The taxa Dicot has 4 species co-occurring with indicated crops.

	The taxa Insect has 2 species co-occurring with indicated crops.

	The taxa Mammal has 2 species co-occurring with indicated crops.

	The taxa Monocot has 1 species co-occurring with indicated crops.

	The taxa Reptile has 1 species co-occurring with indicated crops.

	Iowa

	The taxa Bird has 2 species co-occurring with indicated crops.

	The taxa Bivalve has 2 species co-occurring with indicated crops.

	The taxa Dicot has 3 species co-occurring with indicated crops.

	The taxa Ferns has 1 species co-occurring with indicated crops.

	The taxa Fish has 2 species co-occurring with indicated crops.

12/4/2007 10:34:09 AM   Ver. 2.10.3	Page 5 of 15

	AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS,
KY, LA, ME, MD, MA, MI, 

	MN, MS, MO, MT, NE, NV, NH, NJ, NM, NY, NC, ND, OH, OK, OR, PA, PR, RI,
SC, SD, TN, 

	TX, UT, VT, VA, WA, WV, WI, WY

	The taxa Gastropod has 1 species co-occurring with indicated crops.

	The taxa Mammal has 1 species co-occurring with indicated crops.

	The taxa Monocot has 2 species co-occurring with indicated crops.

	Kansas

	The taxa Bird has 3 species co-occurring with indicated crops.

	The taxa Dicot has 1 species co-occurring with indicated crops.

	The taxa Fish has 4 species co-occurring with indicated crops.

	The taxa Insect has 1 species co-occurring with indicated crops.

	The taxa Mammal has 2 species co-occurring with indicated crops.

	The taxa Monocot has 1 species co-occurring with indicated crops.

	Kentucky

	The taxa Bird has 6 species co-occurring with indicated crops.

	The taxa Bivalve has 22 species co-occurring with indicated crops.

	The taxa Crustacean has 1 species co-occurring with indicated crops.

	The taxa Dicot has 10 species co-occurring with indicated crops.

	The taxa Fish has 4 species co-occurring with indicated crops.

	The taxa Insect has 1 species co-occurring with indicated crops.

	The taxa Mammal has 3 species co-occurring with indicated crops.

	Louisiana

	The taxa Bird has 5 species co-occurring with indicated crops.

	The taxa Bivalve has 3 species co-occurring with indicated crops.

	The taxa Dicot has 2 species co-occurring with indicated crops.

	The taxa Ferns has 1 species co-occurring with indicated crops.

	The taxa Fish has 2 species co-occurring with indicated crops.

	The taxa Mammal has 1 species co-occurring with indicated crops.

	The taxa Reptile has 7 species co-occurring with indicated crops.

	Maine

	The taxa Bird has 2 species co-occurring with indicated crops.

	The taxa Dicot has 1 species co-occurring with indicated crops.

12/4/2007 10:34:09 AM   Ver. 2.10.3	Page 6 of 15

	AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS,
KY, LA, ME, MD, MA, MI, 

	MN, MS, MO, MT, NE, NV, NH, NJ, NM, NY, NC, ND, OH, OK, OR, PA, PR, RI,
SC, SD, TN, 

	TX, UT, VT, VA, WA, WV, WI, WY

	The taxa Fish has 2 species co-occurring with indicated crops.

	The taxa Mammal has 1 species co-occurring with indicated crops.

	The taxa Monocot has 2 species co-occurring with indicated crops.

	The taxa Reptile has 1 species co-occurring with indicated crops.

	Maryland

	The taxa Bird has 1 species co-occurring with indicated crops.

	The taxa Bivalve has 1 species co-occurring with indicated crops.

	The taxa Dicot has 4 species co-occurring with indicated crops.

	The taxa Fish has 2 species co-occurring with indicated crops.

	The taxa Insect has 2 species co-occurring with indicated crops.

	The taxa Mammal has 2 species co-occurring with indicated crops.

	The taxa Monocot has 2 species co-occurring with indicated crops.

	The taxa Reptile has 5 species co-occurring with indicated crops.

	Massachusetts

	The taxa Bird has 3 species co-occurring with indicated crops.

	The taxa Dicot has 1 species co-occurring with indicated crops.

	The taxa Fish has 1 species co-occurring with indicated crops.

	The taxa Insect has 3 species co-occurring with indicated crops.

	The taxa Mammal has 1 species co-occurring with indicated crops.

	The taxa Monocot has 2 species co-occurring with indicated crops.

	The taxa Reptile has 6 species co-occurring with indicated crops.

	Michigan

	The taxa Bird has 2 species co-occurring with indicated crops.

	The taxa Bivalve has 2 species co-occurring with indicated crops.

	The taxa Dicot has 4 species co-occurring with indicated crops.

	The taxa Ferns has 1 species co-occurring with indicated crops.

	The taxa Insect has 4 species co-occurring with indicated crops.

	The taxa Mammal has 3 species co-occurring with indicated crops.

	The taxa Monocot has 3 species co-occurring with indicated crops.

12/4/2007 10:34:09 AM   Ver. 2.10.3	Page 7 of 15

	AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS,
KY, LA, ME, MD, MA, MI, 

	MN, MS, MO, MT, NE, NV, NH, NJ, NM, NY, NC, ND, OH, OK, OR, PA, PR, RI,
SC, SD, TN, 

	TX, UT, VT, VA, WA, WV, WI, WY

	The taxa Reptile has 1 species co-occurring with indicated crops.

	Minnesota

	The taxa Bird has 1 species co-occurring with indicated crops.

	The taxa Bivalve has 2 species co-occurring with indicated crops.

	The taxa Dicot has 2 species co-occurring with indicated crops.

	The taxa Fish has 1 species co-occurring with indicated crops.

	The taxa Insect has 1 species co-occurring with indicated crops.

	The taxa Mammal has 2 species co-occurring with indicated crops.

	The taxa Monocot has 2 species co-occurring with indicated crops.

	Mississippi

	The taxa Amphibian has 1 species co-occurring with indicated crops.

	The taxa Bird has 5 species co-occurring with indicated crops.

	The taxa Bivalve has 9 species co-occurring with indicated crops.

	The taxa Dicot has 2 species co-occurring with indicated crops.

	The taxa Ferns has 1 species co-occurring with indicated crops.

	The taxa Fish has 3 species co-occurring with indicated crops.

	The taxa Mammal has 3 species co-occurring with indicated crops.

	The taxa Reptile has 9 species co-occurring with indicated crops.

	Missouri

	The taxa Bird has 2 species co-occurring with indicated crops.

	The taxa Bivalve has 6 species co-occurring with indicated crops.

	The taxa Crustacean has 1 species co-occurring with indicated crops.

	The taxa Dicot has 7 species co-occurring with indicated crops.

	The taxa Fish has 7 species co-occurring with indicated crops.

	The taxa Gastropod has 1 species co-occurring with indicated crops.

	The taxa Insect has 2 species co-occurring with indicated crops.

	The taxa Mammal has 2 species co-occurring with indicated crops.

	The taxa Monocot has 1 species co-occurring with indicated crops.

	Montana

12/4/2007 10:34:09 AM   Ver. 2.10.3	Page 8 of 15

	AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS,
KY, LA, ME, MD, MA, MI, 

	MN, MS, MO, MT, NE, NV, NH, NJ, NM, NY, NC, ND, OH, OK, OR, PA, PR, RI,
SC, SD, TN, 

	TX, UT, VT, VA, WA, WV, WI, WY

	The taxa Bird has 3 species co-occurring with indicated crops.

	The taxa Dicot has 2 species co-occurring with indicated crops.

	The taxa Fish has 5 species co-occurring with indicated crops.

	The taxa Mammal has 3 species co-occurring with indicated crops.

	Nebraska

	The taxa Bird has 3 species co-occurring with indicated crops.

	The taxa Dicot has 2 species co-occurring with indicated crops.

	The taxa Fish has 2 species co-occurring with indicated crops.

	The taxa Insect has 1 species co-occurring with indicated crops.

	The taxa Mammal has 1 species co-occurring with indicated crops.

	The taxa Monocot has 1 species co-occurring with indicated crops.

	Nevada

	The taxa Bird has 2 species co-occurring with indicated crops.

	The taxa Dicot has 8 species co-occurring with indicated crops.

	The taxa Fish has 23 species co-occurring with indicated crops.

	The taxa Insect has 2 species co-occurring with indicated crops.

	The taxa Monocot has 1 species co-occurring with indicated crops.

	The taxa Reptile has 1 species co-occurring with indicated crops.

	New Hampshire

	The taxa Bivalve has 1 species co-occurring with indicated crops.

	The taxa Dicot has 1 species co-occurring with indicated crops.

	The taxa Insect has 1 species co-occurring with indicated crops.

	The taxa Mammal has 1 species co-occurring with indicated crops.

	The taxa Monocot has 1 species co-occurring with indicated crops.

	The taxa Reptile has 1 species co-occurring with indicated crops.

	New Jersey

	The taxa Bird has 2 species co-occurring with indicated crops.

	The taxa Dicot has 2 species co-occurring with indicated crops.

	The taxa Fish has 1 species co-occurring with indicated crops.

12/4/2007 10:34:09 AM   Ver. 2.10.3	Page 9 of 15

	AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS,
KY, LA, ME, MD, MA, MI, 

	MN, MS, MO, MT, NE, NV, NH, NJ, NM, NY, NC, ND, OH, OK, OR, PA, PR, RI,
SC, SD, TN, 

	TX, UT, VT, VA, WA, WV, WI, WY

	The taxa Mammal has 1 species co-occurring with indicated crops.

	The taxa Monocot has 3 species co-occurring with indicated crops.

	The taxa Reptile has 5 species co-occurring with indicated crops.

	New Mexico

	The taxa Amphibian has 1 species co-occurring with indicated crops.

	The taxa Bird has 6 species co-occurring with indicated crops.

	The taxa Crustacean has 2 species co-occurring with indicated crops.

	The taxa Dicot has 13 species co-occurring with indicated crops.

	The taxa Fish has 13 species co-occurring with indicated crops.

	The taxa Gastropod has 5 species co-occurring with indicated crops.

	The taxa Mammal has 5 species co-occurring with indicated crops.

	The taxa Reptile has 1 species co-occurring with indicated crops.

	New York

	The taxa Bird has 2 species co-occurring with indicated crops.

	The taxa Bivalve has 1 species co-occurring with indicated crops.

	The taxa Dicot has 4 species co-occurring with indicated crops.

	The taxa Ferns has 1 species co-occurring with indicated crops.

	The taxa Fish has 1 species co-occurring with indicated crops.

	The taxa Gastropod has 1 species co-occurring with indicated crops.

	The taxa Insect has 1 species co-occurring with indicated crops.

	The taxa Mammal has 1 species co-occurring with indicated crops.

	The taxa Monocot has 1 species co-occurring with indicated crops.

	The taxa Reptile has 6 species co-occurring with indicated crops.

	North Carolina

	The taxa Arachnid has 1 species co-occurring with indicated crops.

	The taxa Bird has 4 species co-occurring with indicated crops.

	The taxa Bivalve has 8 species co-occurring with indicated crops.

	The taxa Dicot has 21 species co-occurring with indicated crops.

	The taxa Fish has 4 species co-occurring with indicated crops.

12/4/2007 10:34:09 AM   Ver. 2.10.3	Page 10 of 15

	AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS,
KY, LA, ME, MD, MA, MI, 

	MN, MS, MO, MT, NE, NV, NH, NJ, NM, NY, NC, ND, OH, OK, OR, PA, PR, RI,
SC, SD, TN, 

	TX, UT, VT, VA, WA, WV, WI, WY

	The taxa Gastropod has 1 species co-occurring with indicated crops.

	The taxa Insect has 1 species co-occurring with indicated crops.

	The taxa Mammal has 4 species co-occurring with indicated crops.

	The taxa Monocot has 5 species co-occurring with indicated crops.

	The taxa Reptile has 5 species co-occurring with indicated crops.

	North Dakota

	The taxa Bird has 3 species co-occurring with indicated crops.

	The taxa Fish has 1 species co-occurring with indicated crops.

	The taxa Monocot has 1 species co-occurring with indicated crops.

	Ohio

	The taxa Bird has 1 species co-occurring with indicated crops.

	The taxa Bivalve has 6 species co-occurring with indicated crops.

	The taxa Dicot has 4 species co-occurring with indicated crops.

	The taxa Fish has 1 species co-occurring with indicated crops.

	The taxa Insect has 4 species co-occurring with indicated crops.

	The taxa Mammal has 2 species co-occurring with indicated crops.

	The taxa Monocot has 2 species co-occurring with indicated crops.

	The taxa Reptile has 2 species co-occurring with indicated crops.

	Oklahoma

	The taxa Bird has 6 species co-occurring with indicated crops.

	The taxa Bivalve has 2 species co-occurring with indicated crops.

	The taxa Fish has 4 species co-occurring with indicated crops.

	The taxa Insect has 1 species co-occurring with indicated crops.

	The taxa Mammal has 3 species co-occurring with indicated crops.

	The taxa Monocot has 2 species co-occurring with indicated crops.

	Oregon

	The taxa Bird has 4 species co-occurring with indicated crops.

	The taxa Crustacean has 1 species co-occurring with indicated crops.

	The taxa Dicot has 11 species co-occurring with indicated crops.

12/4/2007 10:34:09 AM   Ver. 2.10.3	Page 11 of 15

	AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS,
KY, LA, ME, MD, MA, MI, 

	MN, MS, MO, MT, NE, NV, NH, NJ, NM, NY, NC, ND, OH, OK, OR, PA, PR, RI,
SC, SD, TN, 

	TX, UT, VT, VA, WA, WV, WI, WY

	The taxa Fish has 22 species co-occurring with indicated crops.

	The taxa Insect has 2 species co-occurring with indicated crops.

	The taxa Mammal has 1 species co-occurring with indicated crops.

	The taxa Monocot has 2 species co-occurring with indicated crops.

	The taxa Reptile has 3 species co-occurring with indicated crops.

	Pennsylvania

	The taxa Bird has 1 species co-occurring with indicated crops.

	The taxa Bivalve has 2 species co-occurring with indicated crops.

	The taxa Mammal has 2 species co-occurring with indicated crops.

	The taxa Monocot has 2 species co-occurring with indicated crops.

	The taxa Reptile has 1 species co-occurring with indicated crops.

	Rhode Island

	The taxa Bird has 1 species co-occurring with indicated crops.

	The taxa Dicot has 1 species co-occurring with indicated crops.

	The taxa Fish has 1 species co-occurring with indicated crops.

	The taxa Insect has 1 species co-occurring with indicated crops.

	The taxa Mammal has 1 species co-occurring with indicated crops.

	The taxa Monocot has 1 species co-occurring with indicated crops.

	The taxa Reptile has 4 species co-occurring with indicated crops.

	South Carolina

	The taxa Amphibian has 1 species co-occurring with indicated crops.

	The taxa Bird has 4 species co-occurring with indicated crops.

	The taxa Bivalve has 1 species co-occurring with indicated crops.

	The taxa Dicot has 12 species co-occurring with indicated crops.

	The taxa Ferns has 1 species co-occurring with indicated crops.

	The taxa Fish has 1 species co-occurring with indicated crops.

	The taxa Mammal has 1 species co-occurring with indicated crops.

	The taxa Monocot has 6 species co-occurring with indicated crops.

	The taxa Reptile has 6 species co-occurring with indicated crops.

12/4/2007 10:34:09 AM   Ver. 2.10.3	Page 12 of 15

	AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS,
KY, LA, ME, MD, MA, MI, 

	MN, MS, MO, MT, NE, NV, NH, NJ, NM, NY, NC, ND, OH, OK, OR, PA, PR, RI,
SC, SD, TN, 

	TX, UT, VT, VA, WA, WV, WI, WY

	South Dakota

	The taxa Bird has 3 species co-occurring with indicated crops.

	The taxa Fish has 2 species co-occurring with indicated crops.

	The taxa Insect has 1 species co-occurring with indicated crops.

	The taxa Mammal has 1 species co-occurring with indicated crops.

	The taxa Monocot has 1 species co-occurring with indicated crops.

	Tennessee

	The taxa Arachnid has 1 species co-occurring with indicated crops.

	The taxa Bird has 3 species co-occurring with indicated crops.

	The taxa Bivalve has 38 species co-occurring with indicated crops.

	The taxa Crustacean has 1 species co-occurring with indicated crops.

	The taxa Dicot has 17 species co-occurring with indicated crops.

	The taxa Ferns has 1 species co-occurring with indicated crops.

	The taxa Fish has 16 species co-occurring with indicated crops.

	The taxa Gastropod has 3 species co-occurring with indicated crops.

	The taxa Mammal has 3 species co-occurring with indicated crops.

	The taxa Monocot has 2 species co-occurring with indicated crops.

	Texas

	The taxa Amphibian has 4 species co-occurring with indicated crops.

	The taxa Arachnid has 10 species co-occurring with indicated crops.

	The taxa Bird has 12 species co-occurring with indicated crops.

	The taxa Crustacean has 1 species co-occurring with indicated crops.

	The taxa Dicot has 27 species co-occurring with indicated crops.

	The taxa Fish has 9 species co-occurring with indicated crops.

	The taxa Gastropod has 1 species co-occurring with indicated crops.

	The taxa Insect has 9 species co-occurring with indicated crops.

	The taxa Mammal has 5 species co-occurring with indicated crops.

	The taxa Monocot has 3 species co-occurring with indicated crops.

	The taxa Reptile has 6 species co-occurring with indicated crops.

12/4/2007 10:34:09 AM   Ver. 2.10.3	Page 13 of 15

	AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS,
KY, LA, ME, MD, MA, MI, 

	MN, MS, MO, MT, NE, NV, NH, NJ, NM, NY, NC, ND, OH, OK, OR, PA, PR, RI,
SC, SD, TN, 

	TX, UT, VT, VA, WA, WV, WI, WY

	Utah

	The taxa Bird has 2 species co-occurring with indicated crops.

	The taxa Dicot has 22 species co-occurring with indicated crops.

	The taxa Fish has 8 species co-occurring with indicated crops.

	The taxa Mammal has 2 species co-occurring with indicated crops.

	The taxa Monocot has 2 species co-occurring with indicated crops.

	The taxa Reptile has 1 species co-occurring with indicated crops.

	Vermont

	The taxa Bivalve has 1 species co-occurring with indicated crops.

	The taxa Dicot has 1 species co-occurring with indicated crops.

	The taxa Mammal has 1 species co-occurring with indicated crops.

	The taxa Monocot has 1 species co-occurring with indicated crops.

	Virginia

	The taxa Amphibian has 1 species co-occurring with indicated crops.

	The taxa Bird has 2 species co-occurring with indicated crops.

	The taxa Bivalve has 21 species co-occurring with indicated crops.

	The taxa Crustacean has 2 species co-occurring with indicated crops.

	The taxa Dicot has 13 species co-occurring with indicated crops.

	The taxa Fish has 7 species co-occurring with indicated crops.

	The taxa Gastropod has 1 species co-occurring with indicated crops.

	The taxa Insect has 3 species co-occurring with indicated crops.

	The taxa Mammal has 5 species co-occurring with indicated crops.

	The taxa Monocot has 4 species co-occurring with indicated crops.

	The taxa Reptile has 5 species co-occurring with indicated crops.

	Washington

	The taxa Bird has 4 species co-occurring with indicated crops.

	The taxa Dicot has 7 species co-occurring with indicated crops.

	The taxa Fish has 19 species co-occurring with indicated crops.

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with indicated crops.

12/4/2007 10:34:09 AM   Ver. 2.10.3	Page 14 of 15

	AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS,
KY, LA, ME, MD, MA, MI, 

	MN, MS, MO, MT, NE, NV, NH, NJ, NM, NY, NC, ND, OH, OK, OR, PA, PR, RI,
SC, SD, TN, 

	TX, UT, VT, VA, WA, WV, WI, WY

	The taxa Mammal has 5 species co-occurring with indicated crops.

	The taxa Reptile has 2 species co-occurring with indicated crops.

	West Virginia

	The taxa Amphibian has 1 species co-occurring with indicated crops.

	The taxa Bivalve has 5 species co-occurring with indicated crops.

	The taxa Dicot has 4 species co-occurring with indicated crops.

	The taxa Gastropod has 1 species co-occurring with indicated crops.

	The taxa Mammal has 5 species co-occurring with indicated crops.

	The taxa Monocot has 1 species co-occurring with indicated crops.

	Wisconsin

	The taxa Bird has 3 species co-occurring with indicated crops.

	The taxa Bivalve has 2 species co-occurring with indicated crops.

	The taxa Dicot has 4 species co-occurring with indicated crops.

	The taxa Insect has 2 species co-occurring with indicated crops.

	The taxa Mammal has 2 species co-occurring with indicated crops.

	The taxa Monocot has 2 species co-occurring with indicated crops.

	Wyoming

	The taxa Dicot has 2 species co-occurring with indicated crops.

	The taxa Fish has 1 species co-occurring with indicated crops.

	The taxa Mammal has 4 species co-occurring with indicated crops.

	No species were excluded.

	Dispersed species included in report.

12/4/2007 10:34:09 AM   Ver. 2.10.3	Page 15 of 15

  Total residue half-lives were calculated using the summed 
chlorantraniliprole concentration  (expressed as percent applied) in the
water pre-soak and acetonitrile/water + acid/surfactants or concentrated
acid at evaluated temperature soil extracts.  

 PAGE   

 PAGE   2 

