Unclassified
ENV/
JM/
MONO(
2003)
16
Organisation
de
Coopération
et
de
Développement
Economiques
Organisation
for
Economic
Co­
operation
and
Development
18­
Dec­
2003
___________________________________________________________________________________________
_____________
English
­
Or.
English
ENVIRONMENT
DIRECTORATE
JOINT
MEETING
OF
THE
CHEMICALS
COMMITTEE
AND
THE
WORKING
PARTY
ON
CHEMICALS,
PESTICIDES
AND
BIOTECHNOLOGY
GUIDANCE
DOCUMENT
ON
REPORTING
SUMMARY
INFORMATION
ON
ENVIRONMENTAL,
OCCUPATIONAL
AND
CONSUMER
EXPOSURE
JT00156125
Document
complet
disponible
sur
OLIS
dans
son
format
d'origine
Complete
document
available
on
OLIS
in
its
original
format
ENV/

JM/

MONO(

2003)

16
Unclassified
English
­

Or.

English
ENV/
JM/
MONO(
2003)
16
1
OECD
Environment,
Health
and
Safety
Publications
Series
on
Testing
and
Assessment
No.
42
Guidance
Document
on
Reporting
Summary
Information
on
Environmental,
Occupational
and
Consumer
Exposure
ENV/
JM/
MONO(
2003)
16
2
Acknowledgements
This
Guidance
Document
was
developed
by
the
Ad­
hoc
Expert
Group
on
Reporting
Summary
Exposure
Information,
consisting
of
the
following
experts
nominated
by
member
countries
and
other
organizations:

 
Chris
LEE­
STEERE,
Environment
Australia
 
Edward
DOYLE,
Health
Canada
 
Jonathan
TIGNER,
Environment
Canada
 
Aurélie
CHÉZEAU,
Institut
national
de
l'environnement
industriel
et
des
risques,
France
 
Heinz
GORALCZYK,
Federal
Environmental
Agency,
Germany
 
Gerhard
HEINEMEYER,
Federal
Institute
for
Health
Protection
of
Consumers
and
Veterinary
Medicine,
Germany
 
Leonello
ATTIAS,
Istituto
Superiore
di
Sanità,
Italy
 
Renato
CABELLA,
Istituto
Superiore
per
la
Prevenzione
e
la
Sicurezza
del
Lavoro
(
ISPESL),
Italy
 
Fukuya
IINO,
National
Institute
of
Advanced
Industrial
Science
and
Tech
(
AIST),
Japan
 
Gregory
MOORE,
National
Chemicals
Inspectorate
(
KEMI),
Sweden
 
Diane
LLEWELLYN,
Health
and
Safety
Executive
(
HSE),
UK
 
Cathy
FEHRENBACHER,
US
EPA
(
Chair)
 
Scott
PROTHERO,
US
EPA
 
Bo
WAHLSTRÖM,
UNEP
Chemicals
 
Jennifer
ABRIL,
American
Chemistry
Council
 
James
COOPER,
Association
Management
Center
 
Alvaro
DECARVALHO,
The
Soap
and
Detergent
Association
 
William
GREGGS,
Procter
&
Gamble
 
Volker
KOCH,
Clariant
GmbH
 
Chris
MONEY,
Exxon
Mobil
Petroleum
and
Chemical
 
Jean­
Paul
ROBIN,
MD
Noranda
Inc.

In
addition,
the
following
experts
participated
in
the
trial
of
the
draft
version
of
reporting
formats.

 
Andrea
Boehncke,
Fraunhofer
Institute
of
Toxicology
and
Aerosol
Research,
Germany
 
Haruyuki
Higashino,
National
Institute
of
Advanced
Industrial
Science
and
Technology,
Japan
 
Kyoko
Ono,
National
Institute
of
Advanced
Industrial
Science
and
Technology,
Japan
 
Hongbin
Cao,
National
Institute
of
Advanced
Industrial
Science
and
Technology,
Japan
 
Ron
Lee,
Versar
Inc.,
USA
 
Tim
Brenza,
Eastern
Research
Group
Inc.,
USA
 
Anonymous,
Environment
Agency,
UK
 
Dave
Brooke,
Building
Research
Establishment,
UK
 
Jason
McEwan
and
Jonathan
Tigner,
Environment
Canada
 
Ellen
Stephens,
First
Chemical
Corporation,
USA
ENV/
JM/
MONO(
2003)
16
3
Also
published
in
the
Series
on
Testing
and
Assessment:

No.
1,
Guidance
Document
for
the
Development
of
OECD
Guidelines
for
Testing
of
Chemicals
(
1993;
reformatted
1995)

No.
2,
Detailed
Review
Paper
on
Biodegradability
Testing
(
1995)

No.
3,
Guidance
Document
for
Aquatic
Effects
Assessment
(
1995)

No.
4,
Report
of
the
OECD
Workshop
on
Environmental
Hazard/
Risk
Assessment
(
1995)

No.
5,
Report
of
the
SETAC/
OECD
Workshop
on
Avian
Toxicity
Testing
(
1996)

No.
6,
Report
of
the
Final
Ring­
test
of
the
Daphnia
magna
Reproduction
Test
(
1997)

No.
7,
Guidance
Document
on
Direct
Phototransformation
of
Chemicals
in
Water
(
1997)

No.
8,
Report
of
the
OECD
Workshop
on
Sharing
Information
about
New
Industrial
Chemicals
Assessment
(
1997)

No.
9,
Guidance
Document
for
the
Conduct
of
Studies
of
Occupational
Exposure
to
Pesticides
during
Agricultural
Application
(
1997)

No.
10,
Report
of
the
OECD
Workshop
on
Statistical
Analysis
of
Aquatic
Toxicity
Data
(
1998)

No.
11,
Detailed
Review
Paper
on
Aquatic
Testing
Methods
for
Pesticides
and
industrial
Chemicals
(
1998)

No.
12,
Detailed
Review
Document
on
Classification
Systems
for
Germ
Cell
Mutagenicity
in
OECD
Member
Countries
(
1998)

No.
13,
Detailed
Review
Document
on
Classification
Systems
for
Sensitising
Substances
in
OECD
Member
Countries
1998)

No.
14,
Detailed
Review
Document
on
Classification
Systems
for
Eye
Irritation/
Corrosion
in
OECD
Member
Countries
(
1998)

No.
15,
Detailed
Review
Document
on
Classification
Systems
for
Reproductive
Toxicity
in
OECD
Member
Countries
(
1998)

No.
16,
Detailed
Review
Document
on
Classification
Systems
for
Skin
Irritation/
Corrosion
in
OECD
Member
Countries
(
1998)

No.
17,
Environmental
Exposure
Assessment
Strategies
for
Existing
Industrial
Chemicals
in
OECD
Member
Countries
(
1999)
ENV/
JM/
MONO(
2003)
16
4
No.
18,
Report
of
the
OECD
Workshop
on
Improving
the
Use
of
Monitoring
Data
in
the
Exposure
Assessment
of
Industrial
Chemicals
(
2000)

No.
19,
Guidance
Document
on
the
Recognition,
Assessment
and
Use
of
Clinical
Signs
as
Humane
Endpoints
for
Experimental
Animals
used
in
Safety
Evaluation
(
1999)

No.
20,
Revised
Draft
Guidance
Document
for
Neurotoxicity
Testing
(
in
preparation)

No.
21,
Detailed
Review
Paper:
Appraisal
of
Test
Methods
for
Sex
Hormone
Disrupting
Chemicals
(
2000)

No.
22,
Guidance
Document
for
the
Performance
of
Out­
door
Monolith
Lysimeter
Studies
(
2000)

No.
23,
Guidance
Document
on
Aquatic
Toxicity
Testing
of
Difficult
Substances
and
Mixtures
(
2000)

No.
24,
Guidance
Document
on
Acute
Oral
Toxicity
Testing
(
2001)

No.
25,
Detailed
Review
Document
on
Hazard
Classification
Systems
for
Specifics
Target
Organ
Systemic
Toxicity
Repeated
Exposure
in
OECD
Member
Countries
(
2001)

No.
26,
Revised
Analysis
of
Responses
Received
from
Member
Countries
to
the
Questionnaire
on
Regulatory
Acute
Toxicity
Data
Needs
(
2001)

No
27,
Guidance
Document
on
the
Use
of
the
Harmonised
System
for
the
Classification
of
Chemicals
Which
are
Hazardous
for
the
Aquatic
Environment
(
2001)

No
28,
Guidance
Document
for
the
Conduct
of
Skin
Absorption
Studies
(
2004)

No
29,
Guidance
Document
on
Transformation/
Dissolution
of
Metals
and
Metal
Compounds
in
Aqueous
Media
(
2001)

No
30,
Detailed
Review
Document
on
Hazard
Classification
Systems
for
Mixtures
(
2001)

No
31,
Detailed
Review
Paper
on
Non­
Genotoxic
Carcinogens
Detection:
The
Performance
of
In­
Vitro
Cell
Transformation
Assays(
draft)
ENV/
JM/
MONO(
2003)
16
5
No.
32,
Guidance
Notes
for
Analysis
and
Evaluation
of
Repeat­
Dose
Toxicity
Studies
(
2000)

No.
33,
Harmonised
Integrated
Classification
System
for
Human
Health
and
Environmental
Hazards
of
Chemical
Substances
and
Mixtures(
2001)

No.
34,
Guidance
Document
on
the
Development,
Validation
and
Regulatory
Acceptance
of
New
and
Updated
Internationally
Acceptable
Test
Methods
in
Hazard
Assessment
(
in
preparation)

No.
35,
Guidance
notes
for
analysis
and
evaluation
of
chronic
toxicity
and
carcinogenicity
studies
(
2002)

No.
36,
Report
of
the
OECD/
UNEP
Workshop
on
the
use
of
Multimedia
Models
for
estimating
overall
Environmental
Presistence
and
long
range
Transport
in
the
context
of
PBTS/
POPS
Assessment
(
2002)

No.
37,
Detailed
Review
Document
on
Classification
Systems
for
Substances
Which
Pose
an
Aspiration
Hazard
(
2002)

No.
38,
Detailed
Background
Review
of
the
Uterotrophic
Assay
Summary
of
the
Available
Literature
in
Support
of
the
Project
of
the
OECD
Task
Force
on
Endocrine
Disrupters
Testing
and
Assessment
(
EDTA)
to
Standardise
and
Validate
the
Uterotrophic
Assay
(
2003)

No.
39,
Guidance
Document
on
Acute
Inhalation
Toxicity
Testing
(
in
preparation)

No.
40,
Detailed
Review
Document
on
Classification
in
OECD
Member
Countries
of
Substances
and
Mixtures
Which
Cause
Respiratory
Tract
Irritation
and
Corrosion
(
2003)

No.
41,
Detailed
Review
Document
on
Classification
in
OECD
Member
Countries
of
Substances
and
Mixtures
which
in
Contact
with
Water
Release
Toxic
Gases
(
2003)

No.
42,
Guidance
Document
on
Reporting
Summary
Information
on
Environmental,
Occupational
and
Consumer
Exposure
(
2003)
ENV/
JM/
MONO(
2003)
16
6
No.
43,
Draft
Guidance
Document
on
Reproductive
Toxicity
Testing
and
Assessment
(
in
preparation)

No.
44,
Description
of
Selected
Key
Generic
Terms
Used
in
Chemical
Hazard/
Risk
Assessment
(
2003)

©
OECD
2003
Applications
for
permission
to
reproduce
or
translate
all
or
part
of
this
material
should
be
made
to:
Head
of
Publications
Service,
OECD,
2
rue
André­
Pascal,
75775
Paris
Cedex
16,
France
ENV/
JM/
MONO(
2003)
16
7
About
the
OECD
The
Organisation
for
Economic
Co­
operation
and
Development
(
OECD)
is
an
intergovernmental
organisation
in
which
representatives
of
30
industrialised
countries
in
North
America,
Europe
and
the
Pacific,
as
well
as
the
European
Commission,
meet
to
co­
ordinate
and
harmonise
policies,
discuss
issues
of
mutual
concern,
and
work
together
to
respond
to
international
problems.
Most
of
the
OECD's
work
is
carried
out
by
more
than
200
specialised
Committees
and
subsidiary
groups
composed
of
Member
country
delegates.
Observers
from
several
countries
with
special
status
at
the
OECD,
and
from
interested
international
organisations,
attend
many
of
the
OECD's
Workshops
and
other
meetings.
Committees
and
subsidiary
groups
are
served
by
the
OECD
Secretariat,
located
in
Paris,
France,
which
is
organised
into
Directorates
and
Divisions.

The
work
of
the
OECD
related
to
chemical
safety
is
carried
out
in
the
Environment,
Health
and
Safety
Programme.
As
part
of
its
work
on
chemical
testing,
the
OECD
has
issued
several
Council
Decisions
and
Recommendations
(
the
former
legally
binding
on
member
countries),
as
well
as
numerous
Guidance
Documents
and
technical
reports.
The
best
known
of
these
publications,
the
OECD
Test
Guidelines,
is
a
collection
of
methods
used
to
assess
the
hazards
of
chemicals
and
of
chemical
preparations.
These
methods
cover
tests
for
physical
and
chemical
properties,
effects
on
human
health
and
wildlife,
and
accumulation
and
degradation
in
the
environment.
The
OECD
Test
Guidelines
are
recognised
world­
wide
as
the
standard
reference
tool
for
chemical
testing.

More
information
about
the
Environment,
Health
and
Safety
Programme
and
its
publications
(
including
the
Test
Guidelines)
is
available
on
the
OECD's
World
Wide
Web
site
http://
www.
oecd.
org/
ehs/.

The
Environment,
Health
and
Safety
Programme
co­
operates
closely
with
other
international
organisations.
This
document
was
produced
within
the
framework
of
the
Inter­
Organisation
Programme
for
the
Sound
Management
of
Chemicals
(
IOMC).

The
Inter­
Organization
Programme
for
the
Sound
Management
of
Chemicals
(
IOMC)
was
established
in
1995
by
UNEP,
ILO,
FAO,
WHO,
UNIDO
and
the
OECD
(
the
Participating
Organisations),
following
recommendations
made
by
the
1992
UN
Conference
on
Environment
and
Development
to
strengthen
co­
operation
and
increase
international
co­
ordination
in
the
field
of
chemical
safety.
UNITAR
joined
the
IOMC
in
1997
to
become
the
seventh
Participating
Organisation.
The
purpose
of
the
IOMC
is
to
promote
co­
ordination
of
the
policies
and
activities
pursued
by
the
Participating
Organisations,
jointly
or
separately,
to
achieve
the
sound
management
of
chemicals
in
relation
to
human
health
and
the
environment.
ENV/
JM/
MONO(
2003)
16
8
This
publication
is
available
electronically,
at
no
charge.

For
the
complete
text
of
this
and
many
other
Environment,
Health
and
Safety
publications,
consult
the
OECD's
World
Wide
Web
site
(
http://
www.
oecd.
org/
ehs/)

or
contact:

OECD
Environment
Directorate,
Environment,
Health
and
Safety
Division
2
rue
André­
Pascal
75775
Paris
Cedex
16
France
Fax:
(
33­
1)
45
24
16
75
E­
mail:
ehscont@
oecd.
org
ENV/
JM/
MONO(
2003)
16
9
Table
of
contents
CHAPTER
1.
INTRODUCTION..........................................................................................................
10
Purpose
of
the
Exposure
Reporting
Formats.........................................................................................
10
Overview
of
the
Guidance
...................................................................................................................
10
Overview
of
the
Formats
.....................................................................................................................
10
How
to
Use
the
Formats
and
Guidance
................................................................................................
11
Other
Considerations
in
the
Context
of
Exposure
Reporting.................................................................
12
CHAPTER
2.
FORMATS.....................................................................................................................
13
Format
A:
General
Information
and
Overview
of
Exposure
...............................................................
14
Format
B:
Monitoring
Evaluations
....................................................................................................
18
Format
C:
Modeling
Evaluations.
......................................................................................................
20
CHAPTER
3.
FORMAT­
SPECIFIC
GUIDANCE.................................................................................
21
Format
A:
General
Information
­
Instructions
for
Completing
the
Format.
........................................
22
I.
Identification
Information.................................................................................................................
22
II.
Chemical
Information
.....................................................................................................................
22
III.
Purpose
and
Coverage....................................................................................................................
23
IV.
Summary.......................................................................................................................................
24
V.
Production,
Import/
Export
and
Use
Total
Volumes
.........................................................................
24
VI.
Life
Cycle
Steps
Covered
in
this
Report
.....................................................................................
25
VII.
Unassociated
Format
B
and/
or
Format
C
.....................................................................................
29
VIII.
References
.................................................................................................................................
30
Format
B:
Monitoring
Evaluation
­
Instructions
for
Completing
the
Format.
......................................
31
I.
Identification
Information.................................................................................................................
31
II.
Monitoring
Study
Design
and
Description
of
Scenario
Monitored
...................................................
31
III.
Sampling
and
Analytical
Methods.................................................................................................
32
IV.
Results
and
Reliability
Description
...............................................................................................
33
V.
References
......................................................................................................................................
34
Format
C:
Modelling
Evaluation
 
Instructions
for
Completing
the
Format
.......................................
35
I.
Identification
Information.................................................................................................................
35
II.
Modeling
Objective
and
Description
of
Modeled
Scenario
.............................................................
35
III.
Description
of
Model
and
Model
Validation..................................................................................
36
IV.
Inputs,
Outputs,
and
Reliability
Description..................................................................................
37
V.
References
......................................................................................................................................
39
ANNEX
1
INFORMATION
ON
PHYSICAL
AND
CHEMICAL
PROPERTIES,
EXPOSURE
LIMITS
40
ANNEX
2
GLOSSARY
OF
TERMINOLOGY.......................................................................................
41
ANNEX
3
RESOURCES.......................................................................................................................
42
ANNEX
4
LISTING
OF
INDUSTRIAL
CATEGORIES
AND
USE
CATEGORIES..............................
45
ENV/
JM/
MONO(
2003)
16
10
CHAPTER
1.
INTRODUCTION
Purpose
of
the
Exposure
Reporting
Formats
1.
This
document
contains
guidance
for
using
the
summary
exposure
information
reporting
formats,
which
were
developed
by
the
OECD
Ad
Hoc
Group
on
Reporting
Summary
Exposure
Information.

2.
The
objective
of
the
work
of
this
Ad
Hoc
Group
is
to
develop
flexible
formats
and
guidance
for
the
reporting
of
summary
exposure
information
(
quantitative
and
qualitative),
which
can
be
used
in
various
chemical
assessment
programs.

3.
The
purpose
for
developing
such
formats
and
guidance
is:

 
to
enhance
consistency
in
reporting
summary
exposure
information;

 
to
support
reporting
of
different
levels
of
information
(
e.
g.
Qualitative,
Screening
Level,
Comprehensive)
as
appropriate
to
the
purpose
of
the
report
and
the
data
available
to
the
submitter;

 
to
harmonize
definitions;

 
to
promote
transparency
of
reported
exposure
information;

 
to
provide
clarity
on
the
purpose
and
coverage
(
or
scope)
of
information
reported;
and,

 
to
provide
a
consistent
approach
for
describing
the
reliability
of
the
information.

Overview
of
the
Guidance
4.
The
abbreviated
guidance
provides
suggestions
on
the
type
of
information
that
may
be
included
in
each
section
of
the
draft
format.
Because
each
exposure
assessment
will
be
different
(
e.
g.,
tailored
to
the
specifics
of
the
chemical
and
relevant
exposure
scenarios
for
that
chemical),
the
guidance
is
very
general.
The
level
of
detail
that
is
appropriate
for
a
particular
submission,
and
for
different
sections
within
a
submission,
is
based
on
its
purpose
and
the
availability
of
information.
The
guidance
also
provides
suggestions
for
presenting
the
summary
exposure
information
in
a
manner
that
is
transparent
and
enables
the
reader
to
understand
how
the
analysis
was
conducted,
and
the
extent
to
which
potential
exposures
have
been
characterized.
It
also
gives
an
approach
for
providing
the
reader
with
an
understanding
of
the
reliability
of
the
monitoring
data,
modeled
estimates
and
the
overall
exposure
assessment.

Overview
of
the
Formats
5.
The
pathways
that
lead
to
human
and
environmental
exposure
to
chemicals
may
vary
greatly
by
use
pattern
and
receptor
population
(
Figure
1­
1).
The
summary
exposure
reporting
formats
described
in
ENV/
JM/
MONO(
2003)
16
11
these
pages
are
intended
to
be
a
flexible
framework
for
reporting
summary
exposure
information
that
are
adaptable
to
this
wide
range
of
exposure
scenarios
as
well
as
to
different
levels
of
exposure
information.
Therefore,
these
formats
are
not
intended
to
be
prescriptive.
Rather,
they
provide
a
suggested
flow
of
information.
Three
basic
formats
are
provided
to
facilitate
reporting
of
summary
exposure
information
of
interest
to
industry,
governmental
organizations,
other
stakeholders,
and
the
public.
Format
A:
General
Information
and
Overview
of
Exposure
summarizes
information
such
as
the
organization
and
technical
contact
for
the
information
provided
in
the
formats,
the
identity
and
form
of
the
chemical,
its
overall
volumes,
uses
in
commerce,
and
background
to
help
in
framing
information
and
data
provided
in
associated
Formats
B
and
C.
Format
B:
Monitoring
Evaluations
summarizes
data
and
information
on
direct
measurements
of
chemical
exposure
for
specific
use
or
release
scenarios;
and
Format
C:
Modeling
Evaluations
summarizes
data
and
information
generated
by
using
mathematical
models
that
predict
exposure
to
a
chemical
for
specific
use
or
release
scenarios.
Chapter
2
of
this
document
presents
the
three
formats
and
Chapter
3
gives
more
in­
depth
guidance
on
how
to
complete
the
formats.
Each
format
contains
a
suggested
set
of
exposure­
related
sections
covering
different
types
of
information
that
could
be
reported.
Since
uses
and
exposures
vary
by
chemical
and
since
a
submitter's
purpose
and
available
information
may
vary,
the
content
of
each
relevant
section
of
the
exposure
reporting
formats
for
a
given
chemical
will
also
vary.
However
the
goal
is
that
a
completed
summary
report
will
be
sufficiently
complete
and
transparent
to
enable
readers
to
understand
the
summarized
exposures
without
providing
an
excess
of
information
that
is
not
needed.

6.
A
critical
aspect
in
reporting
exposure
information
is
to
provide
an
evaluation
of
the
reliability
of
that
information,
e.
g.
the
inherent
quality
of
the
exposure
monitoring
or
modeling
information,
and
the
methods
and
procedures
for
collecting
and
describing
the
information
to
be
able
to
give
evidence
of
the
clarity
and
plausibility
of
the
findings.
The
guidance
includes
an
approach
for
providing
a
"
Reliability
Score"
for
information
reported
in
both
Format
B:
Monitoring
and
Format
C:
Modeling.

7.
There
are
4
Annexes
included
in
this
document.
Annex
1
includes
a
format
that
can
be
used
when
summary
information
on
physical,
or
chemical
properties
are
to
be
reported.
Annex
2
provides
a
glossary
of
terminology.
Annex
3
provides
relevant
resources
for
emission
scenario
documents,
exposure
factor
references,
function/
product
use
descriptions,
some
available
models,
etc.
Annex
4
includes
a
listing
of
Industrial
Categories
and
Use
Categories.

How
to
Use
the
Formats
and
Guidance
8.
As
noted
above,
the
formats
are
designed
to
be
flexible
and
to
accommodate
both
quantitative
(
e.
g.,
release
rate,
exposure
result)
and
qualitative
information
(
e.
g.,
description
of
source
of
release,
description
of
control
measures),
to
cover
any
chemical
or
category
of
chemicals
from
various
sources,
and
could
contain
a
variety
of
exposure
scenarios
ranging
from
site­
specific
to
national
or
even
regional
summaries
(
See
figure
1­
1
for
various
sources
and
pathways).
As
a
submitter,
you
may
find
it
helpful
to
consult
with
individuals
who
collected
the
available
information,
occupational
hygienists,
engineers,
or
others
who
are
familiar
with
the
chemical
and
associated
exposures
and
releases.
The
formats
may
be
used
to
summarize
information
from
existing
exposure
assessment
reports,
and/
or
information
that
has
not
previously
been
analyzed
and
characterized
in
an
assessment.
You
will
need
to
determine
the
purpose,
scope,
and
level
of
detail
of
your
summary
and
complete
the
formats
accordingly.
For
example,
if
your
report
summarizes
only
those
exposures
associated
with
occupational
activities,
you
would
complete
sections
I
through
IV
of
the
Format
A
and
the
relevant
information
in
section
V
and
VI.
If
there
were
monitoring
or
modeling
information,
Formats
B
and
C
would
be
completed
as
appropriate.
Within
each
format,
you
will
need
to
determine
the
level
of
detail
appropriate
to
transparently
communicate
the
summarized
exposure
information.
Each
format
section
includes
hyperlinks
 
"
See
Guidance"
 
that
take
you
to
additional
detail
to
aide
you
in
completing
the
Format.
From
the
guidance,
a
"
BACK"
hyperlink
will
take
you
back
to
the
section
in
the
Format.
Helpful
Tips
are
included
at
the
beginning
of
each
Format
or
section
to
assist
you
in
ENV/
JM/
MONO(
2003)
16
12
completing
the
format.

9.
For
each
reported
chemical
or
category
of
chemicals,
a
Format
A:
General
Information
and
Overview
of
Exposure
format
will
need
to
be
completed,
since
it
contains
basic
information
about
the
chemical/
category
and
overall
perspective
on
potential
exposures.
Available
monitoring
or
modeling
data
can
be
summarized
in
Format
B:
Monitoring
Evaluations
and/
or
Format
C:
Modeling
Evaluations.
A
chemical
may
have
been
evaluated
in
one
or
more
monitoring
studies
intended
to
measure
human
exposures,
environmental
media
concentrations
or
for
some
other
purpose.
Likewise,
more
than
one
modeling
study
may
have
been
conducted.
Monitoring
Evaluations
and/
or
Modeling
Evaluations
formats
may
be
provided
for
any
activities
for
which
there
is
a
potential
for
human
or
ecological
exposure
(
e.
g.,
general
environmental
monitoring,
outdoor
air
exposures
to
children
in
the
communities
where
the
production
plant(
s)
are
located,
occupational
exposure
to
workers
involved
in
chemical
production,
etc.).
Therefore,
there
may
be
multiple
Monitoring
Evaluations
and
Modeling
Evaluations
formats
included
with
Format
A.
In
some
cases
it
may
not
be
possible
to
relate
the
measured
exposure
or
environmental
media
concentration
from
a
monitoring
study
to
a
particular
activity
(
i.
e.,
to
chemical
production
or
to
the
industrial,
commercial
or
consumer
product
uses
of
the
chemical).
However,
such
general
monitoring
data
may
still
be
useful
for
understanding
overall
exposures.
In
these
cases,
a
Monitoring
Evaluations
format
can
be
used
to
capture
the
information.

10.
From
a
practical
standpoint,
data
and
information
may
be
duplicated
across
the
formats
if
it
helps
improve
clarity,
while
in
other
cases
a
cross
reference
to
information
elsewhere
in
the
formats
may
be
used
to
prevent
unnecessary
duplication
of
data
and
information.

Other
Considerations
in
the
Context
of
Exposure
Reporting
11.
Proprietary
Information.
It
may
be
necessary
to
establish
mechanisms
to
share
exposure
information
in
a
way
that
successfully
addresses
potential
concerns
about
preserving
the
inherent
value
of
this
information.
In
some
cases,
detailed
information
relevant
to
assessments
may
be
considered
proprietary
such
that
information
providers
may
not
want
to
(
or
even
be
able
to)
share
it
with
competitors.
In
addition,
you
may
be
disinclined
to
share
exposure
data
because
of
its
value
for
potential
use
in
a
regulatory
context,
such
as
gaining
product
approvals
(
e.
g.,
compensation
for
toxicity
testing
data,
proprietary
processes).
The
Alliance
for
Chemical
Awareness
has
documented
a
variety
of
creative
data
sharing
mechanisms
that
can
help
in
meeting
the
goals
of
improved
transparency,
while
maintaining
protection
of
confidential
information,
found
at
:
http://
chemicalawareness.
org/
resources/
data.
html
12.
Communicating
with
the
Public.
Obviously,
the
manner
in
which
information
is
presented
to
the
public
can
be
expected
to
be
of
considerable
interest
and
potential
concern.
Providing
caveats
regarding
the
limitations
of
data
because
of
the
scope
and
nature
of
the
exposure
assessment
may
be
helpful
but
will
not
entirely
address
these
problems.
In
some
 
but
certainly
not
all
 
instances,
you
may
be
able
to
overcome
or
resolve
these
concerns.
In
most
cases,
you
will
have
to
assess
these
concerns
as
part
of
the
cost­
benefit
analysis
that
will
need
to
be
undertaken
in
order
to
make
a
decision
in
the
merits
of
providing
summary
exposure
information.
The
Alliance
for
Chemical
Awareness
has
also
developed
resources
for
such
communications,
which
can
be
found
at:

http://
chemicalawareness.
org/
resources/
communications.
html
13.
Anti­
trust
implications.
Finally,
discussions
among
companies
choosing
to
collaboratively
prepare
exposure
reports
may
include
fairly
detailed
information
on
topics
such
as
chemical
products,
uses
and
production
volume.
Depending
upon
the
level
of
detail,
content
and
context
of
those
discussions,
you
may
wish
to
consult
with
legal
counsel
on
the
potential
for
anti­
trust
issues
and
whether
there
are
tools
or
techniques
to
avoid
potential
liability.
ENV/
JM/
MONO(
2003)
16
13
(
e.
g.
Combustion,
natural
sources
etc.)
Production
Industrial
use
Formulation
Private
/
Consumer
use
(
e.
g.
household,
leisure,
hobby,
hygiene)
Air,
Water,
Soil)

Occupational
Exposure
User
Indirect
Exposure
via
Environment
Consumer
Exposure
Non
User
Activity
Human
Exposure
Exposure
of
Environment
Commercial
/
Professional
use
Sources
throughout
lifecycle
(
e.
g.
disposal,
recovery,
etc)

Sources
outside
the
chain
of
commerce
(
e.
g.
combustion,
natural
sources
etc.)
Intentional
and
unintentional
releases
Figure
1­
1.
Routes
of
Chemical
Exposure.
ENV/
JM/
MONO(
2003)
16
14
CHAPTER
2.
FORMATS
14.
This
Chapter
presents
the
blank
formats
A,
B
and
C,
with
helpful
tips
and
Hyperlinks
to
the
relevant
section
of
the
format­
specific
guidance
(
Chapter
3).

Format
A:
General
Information
and
Overview
of
Exposure
See
Guidance
Report
Title:
(
Create
a
title
that
reflects
the
information
provided
in
the
formats.)
See
Guidance
Helpful
Tip:
Information
should
be
added
under
each
section
if
that
information
is
applicable
to
the
Purpose
and
Coverage
described
in
Format
A,
Section
III.
For
example,
if
the
summary
includes
information
relevant
only
to
worker
exposure,
data
and
information
relevant
to
releases
need
not
be
included
unless
they
are
related
to
the
worker
exposures
being
summarized.

Helpful
Tip:
Data
and
information
may
be
duplicated
across
the
formats
if
it
helps
to
improve
the
clarity,
but
a
cross
reference
to
information
elsewhere
in
the
formats
may
be
used
to
prevent
unnecessary
duplication
of
data
and
information.

Helpful
Tip:
Available
data
tables
may
be
attached
either
as
an
annex
or
within
the
relevant
field.

I.
Identification
Information
(
1)
Date
of
Submission
(
Provide
the
date
on
which
the
summary
was
completed.)

(
2)
Identity
of
Organization
(
Provide
the
company
name
and
technical
contact
information.)
See
Guidance
(
3)
Contents
(
list
of
accompanying
format(
s)
and
annex(
es)
included)
(
List
the
formats
completed,
and
any
annexes)
See
Guidance
II.
Substance
information
(
1)
Category
Name
or
CAS
Number(
s)
(
Provide
CAS
number(
s)
for
the
chemical
and
for
each
chemical
in
the
category
if
a
category
approach
is
used.)
See
Guidance
(
2)
Substance
Name(
s)
(
List
the
chemical
identities
(
trade
names,
common
names,
TSCA
Inventory
names,
IUPAC
names,
and/
or
synonyms.)
See
Guidance
(
3)
Substance
Formula
and
Structure
(
Provide
the
chemical
formula
for
the
substance
and
a
structural
diagram,
if
available.)
See
Guidance
(
4)
Physical
Form
(
Enter
the
physical
form
of
the
pure
chemical
.)
See
Guidance
(
5)
Other
Constituents
(
If
Applicable)
(
List
any
other
constituents
of
the
substance,
including
the
name,
CAS
number,
percentage
range,
impurities,
etc.)
See
Guidance
ENV/
JM/
MONO(
2003)
16
15
III.
Purpose
and
Coverage
of
this
Report.

(
1)
Purpose
(
Provide
a
brief
description
of
the
purpose
of
the
submission
e.
g.,
a
post­
SIDS
submission.)
See
Guidance
(
2)
Coverage
(
Identify
which
exposures
are
covered
in
this
summary,
and
which
are
not
covered)
See
Guidance
IV.
Summary
(
1)
Synthesis
of
Key
Results
(
Summarize
the
key
results
of
the
exposure
assessment,
including
the
most
significant
endpoints
of
exposure,
and
the
methods
by
which
they
were
identified
and
quantified.)
See
Guidance
(
2)
Summary
of
Data
Collection
Efforts
(
Describe
the
efforts
to
research
and
collect
data
for
this
summary.)
See
Guidance
(
3)
Discussion
of
Key
Uncertainties,
Limitations,
Data
Gaps
(
Describe
the
uncertainties
and
limitations
of
the
information
and
data
reported.)
See
Guidance
(
4)
Table
of
Exposure
Results
(
List
the
exposure
results
and
identify
the
exposed
population(
s).)
See
Guidance
V.
Production,
Import/
Export
and
Use
Total
Volumes
(
1)
Estimated
Total
Produced,
Imported,
and
Exported
Volumes:
(
Provide
volumes
in
tonnes
per
year;
indicate
information
source,
the
geographical
area
and
year
to
which
the
value
applies.)
See
Guidance
(
2)
Industrial
and
Use
Categories
and
Percent
Volume
for
Each:
(
For
each
Industrial
Category
or
Use
Category,
provide
the
corresponding
percentage
of
chemical
used
indicate
source
of
information,
the
geographical
area
and
year
to
which
the
value
applies.)
See
Guidance
(
3)
Remarks:
(
Include
any
relevant
information
not
included
elsewhere
in
the
format.)
See
Guidance
ENV/
JM/
MONO(
2003)
16
16
VI.
Life
Cycle
Steps
Covered
in
this
Report
See
Guidance
Production,
Formulation,
and
Industrial/
Professional
Use
See
Guidance
Helpful
Tip:
This
section
is
designed
to
be
applicable
to
Production,
Formulation,
and
Use.
Complete
the
section
using
information
relevant
to
the
applicable
part
of
the
life
cycle.

Helpful
Tip:
This
section
may
be
copied
multiple
times
to
be
used
for
each
process
and/
or
site
you
are
including
based
on
the
Purpose
and
Coverage
you've
identified
for
this
report.

Helpful
Tip:
Some
chemicals
are
used
in
private
businesses
that
may
be
characterized
as
industrial
or
nonindustrial
You
should
determine
whether
the
information
and
data
are
more
appropriately
placed
in
the
format
under
the
Industrial/
Professional
Use
(
this
section
of
Format
A)
or
under
Private
Use
(
next
section
of
Format
A).
For
example,
an
assessment
of
solvent
release
and
exposure
in
dry
cleaning
businesses
would
generally
be
summarized
under
Industrial
Use,
whereas
a
solvent
release
from
a
household
would
be
Private
Use.
(
1)
Volumes
and
Related
Information:
(
Provide
general
or
site­
specific
information
on
sites
and
volume
produced,
formulated,
or
used
in
this
process)
See
Guidance
(
2)
Process
Description
and
Related
Information:
(
Describe
the
process
and/
or
provide
a
process
flow
diagram
and
other
relevant
and
available
information.)
See
Guidance
(
3)
General
Description
of
Potential
Releases
and
Exposures
(
a)
Releases:
(
Describe
and
where
possible
quantify
all
potential
sources
of
releases
and
each
receiving
media)
See
Guidance
(
b)
Exposures:
(
Describe
and
where
possible
quantify
all
potential
exposures)
See
Guidance
For
any
releases
and
exposures
presented
in
Formats
B
and
C
provide
a
cross­
reference.
if
applicable.
(
4)
Discussion
of
Factors
that
Decrease
or
Increase
Releases
and
Exposures:
(
Describe
how
engineering,
administrative
or
work
practice
controls,
personal
protective
equipment,
and
occupational
and
environmental
regulations
may
affect
releases
and
exposures.)
See
Guidance
(
5)
Environmental
Exposure:
(
Describe
and
where
possible
quantify
the
discharges
associated
with
the
process)
See
Guidance
(
6)
Information
not
Included
and
Rationale
Briefly
describe
and
explain
why
available
information
relevant
to
the
purpose
and
coverage
of
this
summary
is
not
included.
See
Guidance
(
7)
Remarks:
(
Include
any
relevant
information
not
included
elsewhere
in
the
format.)
See
Guidance
Private
(
Consumer)
Use
(
copy
for
different
use
types)

Helpful
Tip:
Sections
8
through
11
below
apply
only
to
consumer
products.
If
your
report
does
not
include
consumer
products,
this
section
may
be
omitted.

Helpful
Tip:
Some
chemicals
are
used
in
private
businesses
that
may
be
characterized
as
industrial
or
nonindustrial
You
should
determine
whether
the
information
and
data
are
more
appropriately
placed
in
the
format
under
the
Industrial/
Professional
Use
or
under
Private
Use.
For
example,
an
assessment
of
solvent
release
and
exposure
in
dry
cleaning
businesses
would
generally
be
summarized
under
Industrial
Use,
whereas,
a
solvent
release
from
a
household
would
be
Private
Use.
ENV/
JM/
MONO(
2003)
16
17
(
8)
Function/
Product
Use
Category
Description.
Identify
each
type
of
private
(
consumer)
product
use,
function
of
the
substance
in
the
product,
physical
form
of
the
product,
concentration
of
the
substance
in
the
product
and
other
relevant
information.
See
Guidance
(
9)
General
Description
of
Direct
Exposures
to
Private
(
Consumer)
Products
and
of
Potential
Releases
to
the
Environment
leading
to
Ecological
Exposures
and
Indirect
Human
Exposures
(
a)
Exposures:
(
Describe
and
where
possible
quantify
exposures
to
the
products)
See
Guidance
(
b)
Releases:
(
Describe
and
where
possible
quantify
releases
from
the
products)
See
Guidance
For
any
exposures
and
releases
presented
in
Formats
B
and
C,
provide
a
cross­
reference,
if
applicable
(
10)
Discussion
of
Factors
that
Decrease
or
Increase
Releases
and
Exposures:
Discuss
the
effects
of
use
controls,
personal
protective
equipment,
and
waste
disposal
requirements
on
the
exposures
and
releases
described
in
(
9).
See
Guidance
(
11)
Remarks:
(
Use
this
area
to
include
any
relevant
information
not
included
elsewhere
in
the
format.)
See
Guidance
VII.
Unassociated
Format
B
and/
or
Format
C
(
1)
Notes
and
Remarks
on
Unassociated
Format
B
and/
or
Format
C:
(
List
any
copies
of
Format
B
and
Format
C
that
are
not
linked
to
a
monitoring
or
modeling
study
listed
in
Format
A.)
See
Guidance
VIII.
References.

Format
A
References
(
Provide
any
relevant
citations,
resources,
and
references)
See
Guidance
ENV/
JM/
MONO(
2003)
16
18
Format
B:
Monitoring
Evaluations
See
Guidance
Report
Title:
(
Same
as
Format
A
Title.)

Helpful
Tip:
If
your
submission
included
multiple
studies,
you
will
need
to
make
multiple
copies
of
this
form
and
fill
each
copy
out
for
an
individual
study.

Helpful
Tip:
Format
B
is
designed
to
be
flexible
and
to
be
applied
to
different
types
of
monitoring
evaluations
(
human
and
environmental
monitoring.)
Data
can
be
duplicated
in
the
formats
if
it
serves
the
purpose
of
clarity,
but
a
cross­
reference
to
information
elsewhere
in
the
formats
is
sufficient
to
prevent
unnecessary
duplication
of
information.
Also,
there
can
be
a
great
range
of
variability
in
the
level
of
detail
available
for
monitoring
and
modeling
studies.
If
you
do
not
have
the
information
in
the
section,
simply
state
this.

Helpful
Tip:
Available
data
tables
may
be
attached
either
as
an
annex
or
within
the
relevant
field.

I.
Identification
Information
(
1)
Study
Title
(
Brief
description
of
Study)

(
2)
Activity
Associated
with
Monitoring
Information:
(
Identify
the
activity
from
Format
A
to
which
this
release
or
exposure
data
applies)
See
Guidance
II.
Monitoring
Study
Design
and
Description
of
Scenario
Monitored
(
1)
Monitoring
Study
Objective
and
Scenario
Description:
(
Describe
the
study's
design,
scope,
and
objectives
and
the
scenario
being
monitored.)
See
Guidance
III.
Sampling
and
Analytical
Methods
(
1)
Media
Sampled
(
Describe
the
media
sampled
e.
g.
personal
inhalation
monitoring,
biomonitoring,
general
sample
of
water.)
See
Guidance
(
2)
Sampling:
(
Describe
all
aspects
of
the
sampling
procedure
methodology
and
QA/
QC)
See
Guidance
(
3)
Method/
Procedure:
(
Describe
the
analytical
method
used,
including
validation,
detection
limits,
and
QA/
QC)
See
Guidance
IV.
Results
and
Reliability
Description
(
1)
Results:
(
Provide
a
summary
of
the
results
of
the
monitoring
study
and
exposure
estimates
based
on
the
monitoring
data.
See
Guidance
ENV/
JM/
MONO(
2003)
16
19
(
2)
Reliability
Score:
(
Provide
a
score
for
each
release,
environmental
concentration,
or
exposure
(
or
intake
or
dose)
estimate
above.)
See
Guidance
(
3)
Remarks:
(
List
resources
used,
applicable
study
notes,
etc.
for
the
monitoring
study.)
See
Guidance
V.
References
Format
B
References
(
Provide
any
relevant
citations,
resources,
and
references.)
See
Guidance
ENV/
JM/
MONO(
2003)
16
20
Format
C:
Modeling
Evaluations.
See
Guidance
Report
Title:
(
Same
as
Format
A
Title.)

Helpful
Tip:
If
your
submission
included
multiple
studies,
you
will
need
to
make
multiple
copies
of
this
form
and
fill
each
copy
out
for
an
individual
study.

Helpful
Tip:
Format
C
is
designed
to
be
flexible
and
to
be
applied
to
different
types
of
modeling
evaluations
(
human
and
environmental
modeling.)
Data
can
be
duplicated
in
the
formats
if
it
serves
the
purpose
of
clarity,
but
a
cross­
reference
to
information
elsewhere
in
the
formats
is
sufficient
to
prevent
unnecessary
duplication
of
information.
Also,
there
can
be
a
great
range
of
variability
in
the
level
of
detail
available
for
monitoring
and
modeling
studies.
If
you
do
not
have
the
information
in
the
section,
simply
state
this.

Helpful
Tip:
Available
data
tables
may
be
attached
either
as
an
annex
or
within
the
relevant
field.

I.
Identification
Information
(
1)
Study
Title
(
Brief
description
of
Study)

(
2)
Activity
Associated
with
Modeling
Information:
(
List
the
specific
activity
and
description
associated
with
the
modeling
information
from
Format
A,
(
i.
e.,
the
cross­
reference
with
Format
A.)
See
Guidance
II.
Modeling
Objective
and
Description
of
Modeled
Scenario
(
1)
Modeling
Study
Objective
and
Scenario
Description:
(
Explain
the
intent
of
the
study
and
describe
the
scenario
being
modeled)
See
Guidance
III.
Description
of
Model
and
Status
of
Peer
review
and
Validation
(
1)
Tool
or
Model:
(
Provide
the
name
of
the
model,
a
brief
description,
the
model's
version
number,
the
basic
algorithm
if
appropriate
and
the
date
on
which
the
model
was
run.)
See
Guidance
(
2)
Validation/
Peer
Review:
(
Describe
any
existing
peer
reviews
and
the
scope
of
any
validation
of
the
model;
provide
references.)
See
Guidance
(
3)
Availability
and
Documentation:
(
Provide
information
on
how
to
obtain
the
model
and
documentation.)
See
Guidance
IV.
Inputs,
Outputs,
and
Reliability
Description
(
1)
Media
Modeled:
(
Describe
the
type
of
medium
or
matrix
modeled
(
e.
g.,
soil,
clothing
or
patches
of
cloth)
and
how
the
medium
can
affect
the
potential
for
exposure
(
e.
g.
transport
through
soil.))
See
Guidance
ENV/
JM/
MONO(
2003)
16
21
(
2)
Inputs:
(
Provide
the
values
of
key
input
parameters.
If
the
model's
default
values
were
changed,
provide
rationale.)
See
Guidance
(
3)
Estimated
Model
Outputs:
(
List
the
model
results
and
the
release
medium
or
exposed
population
associated
with
each
modeled
value;
characterize
the
results
(
i.
e.,
average,
conservative,
etc.),
and
provide
a
basis)
See
Guidance
(
4)
Reliability
Score.
(
Provide
a
reliability
score
for
each
release,
environmental
concentration,
or
exposure
(
or
intake
or
dose)
estimate
above.)
See
Guidance
(
5)
Remarks:
(
Provide
any
resources
used,
applicable
study
notes,
etc.
for
the
modeling
study
and
any
associated
exposure
estimates.)
See
Guidance
V.
References
(
1)
Format
C
References
(
Provide
any
relevant
citations,
resources,
and
references)
See
Guidance
ENV/
JM/
MONO(
2003)
16
22
CHAPTER
3.
FORMAT­
SPECIFIC
GUIDANCE
15.
This
Chapter
provides
instructions
for
completing
the
exposure
formats,
resources
and
references,
and
glossary
of
terms.
This
also
includes
hyperlinks
to
the
corresponding
fields
in
Chapter
2.

Format
A:
General
Information
­
Instructions
for
Completing
the
Format.
BACK
16.
The
purpose
of
the
Format
A
(
General
Information
and
Overview
of
Exposure)
is
to
provide
identification
and
background
information
such
as
the
originator,
chemical/
category,
purpose
and
coverage
of
the
report,
synthesis
of
results,
volumes,
activities
(
e.
g.
production,
industrial
use,
commercial
use,
consumer
product
use),
release
and
exposure
information
and
measured
data
or
estimates,
and
crossreferences
to
Monitoring
Evaluations
format(
s)
(
Format
B)
and/
or
Modeling
Evaluations
format(
s)
(
Format
C).
Formats
B
and
C
are
used
to
provide
summary
information
on
any
quantitative
exposure
and
release
estimates,
and
the
reliability
of
the
estimates.

Report
Title
BACK
17.
This
field
is
for
creating
an
overall
title
that
reflects
the
scope
of
information
provided
in
the
format(
s),
for
record­
keeping
purposes.
You
should
use
unique
identifiers
to
help
track
records.
If
you
submit
monitoring
or
modeling
summaries,
you
may
also
use
this
field
as
a
means
of
linking
the
information
provided
in
the
other
formats.
For
example,
if
a
single
substance
is
being
evaluated,
the
chemical
name
can
be
used
to
coordinate
the
various
formats.
If
a
category
approach
is
being
used,
then
a
category
name
of
descriptor
can
be
used.

I.
Identification
Information
(
1)
Date
of
Submission
18.
To
further
enhance
record­
keeping,
this
field
is
to
be
filled
out
with
the
date
on
which
the
summary
was
completed.

(
2)
Identity
of
Organization
BACK
19.
This
field
is
for
logistical
purposes,
where
the
respondent
and
technical
contact
information
is
provided.
The
information
can
include
the
organization
name
and
technical
contact
name(
s),
as
well
as
addresses,
phone
numbers,
e­
mail,
web
site
URLs,
or
other
information
the
submitter
deems
relevant.

(
3)
Contents
(
list
of
formats
and
annex
included)
BACK
20.
This
field
is
for
the
reader's
ease
in
understanding
the
layout
of
the
information
provided,
by
a
listing
and
brief
description
of
each
format
included
in
this
report.

II.
Chemical
Information
(
1)
Category
Name
or
CAS
Number(
s)
BACK
21.
The
CAS
number(
s)
should
be
used
as
a
primary
cross­
referencing
identifier
for
synonyms.
If
a
category
approach
is
used,
the
Category
Name
should
be
provided
in
this
field.
ENV/
JM/
MONO(
2003)
16
23
(
2)
Chemical
Name(
s)
BACK
22.
This
field
is
for
listing
the
various
identities
a
product
may
have,
including
trade
names,
common
names,
TSCA
Inventory
names,
IUPAC
names,
and
synonyms.
For
consistency
in
other
geographical
areas,
you
can
use
the
9th
Collective
Index
Chemical
Abstracts
index
name
or
search
the
STN
International
for
the
name
of
the
chemical.
If
a
category
approach
is
used,
the
name
of
each
chemical
in
the
category
and
its
CAS
number
should
be
provided
in
this
field.

(
3)
Substance
Formula
and
Structure
BACK
23.
This
field
is
for
providing
the
chemical
formula
for
the
substance
and
a
structural
diagram,
if
available.

(
4)
Physical
Form
BACK
24.
This
field
is
for
entering
the
physical
form
(
e.
g.
solid,
liquid,
aerosol,
suspension)
of
the
pure
chemical
and,
if
applicable,
of
the
mixture(
s)
containing
the
chemical.
If
a
category
approach
is
used,
it
is
appropriate
to
provide
the
physical
form
for
each
chemical
in
the
category.
This
information
is
important
because
the
physical
form
of
a
product
can
influence
the
potential
for
exposure.
For
example,
some
chemicals
can
be
distributed
in
different
particle
sizes,
which
would
impact
the
likelihood
of
inhalation
exposure.
Also,
in
the
case
of
product
mixtures,
other
ingredients
can
lower
the
boiling
point
of
the
component
being
assessed,
which
could
reduce
the
potential
for
inhalation
exposure.

(
5)
Other
Constituents
(
If
Applicable)
BACK
25.
This
field
is
for
listing
any
other
constituents
of
the
substance,
including
the
name,
CAS
number,
percentage
range,
impurities,
etc,
as
applicable.

III.
Purpose
and
Coverage
(
1)
Purpose
BACK
26.
This
field
is
for
a
brief
description
of
the
purpose
of
the
submission
(
e.
g.,
a
post­
SIDS
summary
report).
This
information
will
help
guide
you
in
determining
which
sections
of
the
format
to
complete
and
assist
the
reader
in
understanding
what
type
of
information
to
expect.

(
2)
Coverage
BACK
27.
This
field
is
for
characterizing
the
extent
to
which
the
summary
covers
the
range
of
potential
exposures
from
production,
processing,
use
and
disposal
and
what
geographic
range
is
addressed.
In
summarizing
and
reporting
exposure
information,
it
is
important
to
communicate
its
thoroughness
and
scope.
This
information
will
also
help
guide
the
reader
on
what
to
expect
and
guide
you
in
determining
which
sections
of
the
format
to
complete.
The
extent
of
coverage
provided
by
an
exposure
report
may
be
evaluated
by
asking
the
following
questions
relating
to
the
assessments
that
comprise
the
submission:

 
Do
the
exposure
studies
provide
a
current
total
chemical
volume,
the
assessed
chemical
volume,
and
how
both
of
these
volumes
are
broken
out
among
uses?
If
they
do
not,
do
the
summaries
provide
an
explanation
of
why
they
did
not
provide
this
information
 
Do
the
summaries
estimate
or
otherwise
address
the
range
of
exposure
scenarios
(
source/
pathway/
route/
population)
that
are
possible
(
at
least
theoretically)?
This
range
of
exposure
scenarios
includes
occupational
exposures,
consumer
product
exposures,
indirect
exposures
to
ENV/
JM/
MONO(
2003)
16
24
humans
from
releases
to
the
environment
and
environmental
(
ecological)
exposures.
If
one
or
more
of
the
scenarios
were
not
addressed,
does
the
summary
provide
an
explanation
of
why
it
was
not
addressed?
Does
the
summary
address
aggregate
exposures?

IV.
Summary
(
1)
Synthesis
of
Key
Results
BACK
28.
This
field
is
for
briefly
summarizing
the
key
results
of
the
reported
information.
Indicate
the
most
significant
endpoints
of
exposure
among
the
potential
exposures
to
the
chemical
being
evaluated.

(
2)
Summary
of
Data
Collection
Efforts
BACK
29.
This
field
is
for
describing
the
extent
of
efforts
involved
in
researching
and
collecting
data
for
this
exposure
summary.

(
3)
Discussion
of
Key
Uncertainties,
Limitations,
and
Data
Gaps
BACK
30.
This
field
is
for
discussing
uncertainties,
key
data
gaps,
restrictions
in
the
representativeness
of
the
data,
etc.,
and
other
limitations.
For
instance,
it
is
understood
that
often
100%
of
total
production
volume
or
uses
will
not
be
precisely
known.
When
this
occurs,
identify
these
limitations
and
the
uncertainties
that
may
stem
from
them.

(
4)
Table
of
Exposure
Results
BACK
31.
This
field
may
be
useful
for
providing
a
tabular
summary
of
quantitative
exposure
information
for
important
scenarios
listing
the
acute
and/
or
chronic
exposures
(
mg/
kg­
day)
and
identifying
the
exposed
population.

V.
Production,
Import/
Export
and
Use
Total
Volumes
(
1)
Estimated
Total
Produced,
Imported,
and
Exported,
Volumes
(
tonnes/
year)
BACK
32.
This
field
is
for
identifying
the
total
estimated
produced,
imported,
and
exported
chemical
volume
for
the
most
recent
calendar
year
available
in
tonnes/
year.
Specify
what
the
numbers
represent,
such
as
production
from
one
company
versus
total
national
or
regional
production,
global
production,
etc
and
to
identify
the
source
of
the
information.
Ranges
may
be
used
as
necessary
to
avoid
disclosure
of
confidential
information.
To
adequately
characterize
the
coverage
of
the
report,
and
its
transparency,
it
is
important
to
describe
what
portion
of
the
chemical
volume
has
been
accounted
for.

(
2)
Industrial
and
Use
Categories
and
Total
Percentage
Volume
for
Each
BACK
33.
This
field
is
for
identifying
the
known
Use
Categories
(
e.
g.,
surfactant,
flame
retardant,
etc.)
for
the
chemical
and
the
percentage
of
estimated
volume
that
is
associated
with
each
category
(
e.
g.,
10%
­
20%
used
in
Use
Category
X).
Also,
identify
the
primary
Industrial
Categories
(
end
uses)
of
the
chemical
and
the
percentage
of
estimated
volume
associated
with
each
use
(
e.
g.,
70%
­
80%
used
in
Industrial
Category
Y).
It
may
be
necessary
to
use
estimates
or
ranges
of
volumes
where
exact
information
is
unavailable
or
to
avoid
the
disclosure
of
confidential
information.
Identify
the
geographic
area
where
the
information
is
applicable.
Annex
4
provides
a
listing
of
the
Industrial
and
Use
Categories,
which
may
be
helpful.
ENV/
JM/
MONO(
2003)
16
25
(
3)
Remarks
BACK
34.
Use
this
field
to
include
any
information
that
would
be
useful
to
the
submission
but
did
not
fit
into
any
other
sections
in
the
format.

VI.
Life
Cycle
Steps
Covered
in
this
Report
BACK
35.
This
section
of
the
format
is
designed
to
be
applicable
to
four
life
cycle
steps
 
production,
formulation,
industrial/
professional
use,
and
private/
consumer
use
 
to
help
you
organize
activity
and
use
information.
Subsections
1
through
7
are
applicable
to
production,
formulation,
and
industrial
use;
subsections
8
through
11
are
applicable
to
private/
consumer
use.
Fill
out
sections
for
the
uses
that
pertain
to
the
chemical
of
interest
and/
or
the
purpose
of
the
summary.
For
example,
an
intermediate
may
be
used
only
as
a
building
block
to
make
another
chemical.
Therefore,
only
information
relating
to
its
production
and
final
use
as
an
intermediate
are
relevant.
The
section
for
private/
consumer
use
would
not
be
filled
out,
nor
would
there
be
any
discussion
of
formulation
or
professional
uses.
Also,
for
submissions
containing
quantitative
information
from
modeling
or
monitoring
data,
you
may
use
this
section
to
specifically
tie
in
studies
summarized
in
Format
B
or
Format
C
to
particular
uses
or
activities.
For
those
studies
that
cannot
be
linked
directly,
you
may
provide
references
to
the
studies
in
Section
VII,
which
follows
this
section.

36.
To
assist
with
organizing
the
information
in
this
section,
which
will
assist
readers
in
following
those
exposures
that
could
result
from
which
processes,
provide
a
thorough
discussion
of
each
process
and
use
separately.
Each
process
and
use
should
be
clearly
labeled
to
avoid
confusion,
especially
for
chemicals
that
have
multiple
uses.

Production/
Formulation/
Industrial/
Professional
Use
BACK
37.
If
relevant
to
the
Purpose
and
Coverage
section,
the
following
sections
for
production,
formulation,
and
industrial
use
may
be
copied
and
used
to
summarize
information
for
each
of
these
process
types
covered.

38.
Some
chemicals
are
used
in
private
businesses
that
may
be
characterized
as
industrial
or
nonindustrial
You
should
determine
whether
the
information
and
data
are
more
appropriately
placed
in
the
format
under
the
Industrial
Use
(
this
section
of
Format
A)
or
under
Private
Use
(
next
section
of
Format
A).
For
example,
an
assessment
of
solvent
release
and
exposure
in
dry
cleaning
businesses
would
generally
be
summarized
under
Industrial
Use,
whereas
a
solvent
release
from
a
household
use
would
be
Private.

(
1)
Volumes
and
Related
Information
BACK
39.
For
each
process,
provide
the
volume
(
tonnes/
yr)
of
pure
substance
produced,
formulated,
or
used
in
this
process
and,
if
available,
the
number
of
sites.
Ranges
may
be
used
as
necessary
to
avoid
disclosure
of
confidential
information.
If
the
substance
is
in
a
formulation
or
mixture,
also
indicate
the
percentage
by
weight
of
the
pure
substance
in
the
formulation
or
mixture.
If
available,
include
site­
specific
information,
including
locations,
geographic
region
or
country,

(
2)
Process
Description
and
Related
Information
BACK
40.
A
process
description
and
related
information
can
provide
useful
information
on
potential
releases
and
exposures
that
are
not
sufficiently
communicated
just
from
chemical
reactions.
In
this
section
a
description
and/
or
a
diagram
may
be
provided
of
the
process
of
production,
formulation,
or
industrial
use
of
the
chemical
or
mixture
containing
the
chemical.
It
includes,
if
available,
factors
which
can
be
relevant
ENV/
JM/
MONO(
2003)
16
26
to
the
description
such
as:

 
where
human
intervention
is
involved,
highlight
activities/
processes
and/
or
tasks
 
volume
of
the
pure
chemical
and
of
the
mixture
containing
the
chemical,
if
applicable,
produced,
formulated,
or
used
per
day,
per
batch,
or
per
year
in
tonnes.
Ranges
may
be
used
as
necessary
to
avoid
disclosure
of
confidential
information.
 
whether
the
production
process
is
continuous
or
batch;
 
whether
the
process
is
open
or
closed;
 
relevant
changes
in
chemical's
physical
form
or
concentration;
 
whether
water
is
involved
in
the
process;
 
cleaning
of
the
process
equipment,
and/
or
in
cleaning
or
rinsing
of
emptied
transport
containers;
 
what
is
done
with
process
and
cleaning
wastes;
and
 
what
types
of
transport
containers
are
used
to
deliver,
store
and
ship
the
chemical
or
mixture
containing
the
chemical.

The
following
questions
can
be
helpful
for
completeness
as
they
indicate
the
next
step
in
the
life
cycle.
Is
the
chemical
or
mixture
containing
the
chemical:

a.
Consumed
internally
for
other
chemical
production
or
use?
b.
Formulated
or
packaged
by
the
producer?
c.
Sold
to
distributors?
d.
Sold
for
use
in
other
chemical
production
(
by
the
producer
or
by
the
distributor)?
e.
Sold
to
formulators
or
repackagers
(
by
the
producer
or
by
the
distributor)?

(
3)
General
Description
of
Potential
Releases
and
Exposures
BACK
41.
This
section
is
one
of
the
most
important
in
Format
A,
helping
to
address
transparency
and
coverage.
It
provides
an
opportunity
to
describe
potential
releases
and
exposures
so
that
readers
have
a
clear
understanding
of
which
releases
pertain
to
which
exposures.
The
submitter
should
organize
the
information
consistently
throughout
the
section,
whether
describing
each
aspect
separately
or
combining
all
relevant
release,
exposure
and
mitigation
information
in
a
continuous
narrative.

42.
a)
Releases:
Releases
are
described
and
cross
referenced
to
related
Format
B
and
C
estimates.

The
summary
identifies
all
likely
sources,
the
likely
receiving
media,
and
whether
the
release
would
be
periodic,
accidental
or
expected.
It
also
includes,
if
available:
 
release
volumes,
from
the
production,
formulation,
or
industrial
use
and
any
other
parts
of
the
life
cycle
of
the
chemical.
 
list
of
point
sources,
release
rate
for
each
source
and
frequency
of
release
(
days/
yr)
 
the
aggregate
(
sum
total)
release
rates
(
daily
or
per
batch
releases
in
tonnes
to
surface
water
or
to
publicly
owned
treatment
works,
as
fugitive
or
stack
air
releases
or
emissions,
to
on­
site
or
off­
site
incineration,
to
landfill
or
applied
to
land
on
or
off
site,
other
transfer
etc.)
 
each
medium
to
which
one
or
more
releases
occurs
It
is
helpful
to
be
as
quantitative
and
precise
as
possible
(
i.
e.,
avoid
the
use
of
words
such
as
significant,
sufficient,
low,
negligible,
etc.,
unless
such
words
can
be
backed
up
by
explanatory
text.)
It
may
be
helpful
to
describe
if
the
chemical
is
directly
released
in
the
media
(
emission
to
surface/
sea
water
or
air
without
treatment)
or
if
there
is
on­
site
treatment
of
the
chemical
(
ventilation
hoods,
air
pollution
control
equipment,
a
wastewater
treatment
plant,
etc.).
ENV/
JM/
MONO(
2003)
16
27
For
each
individual
point
source
estimate,
provide:
 
the
year
to
which
the
estimate
pertains
(
the
most
recent
data
available
is
usually
most
appropriate):
and
either:
 
the
basis
(
monitoring
data,
which
is
preferable,
or
other
appropriate
method),
or:
 
the
cross­
reference
to
Format
B
or
C
in
which
the
estimate
was
reported.

43.
b)
Exposures:
The
summary
identifies
exposures
from
relevant
sources
and
the
likely
exposed
environmental
species
or
human
populations.
It
includes
(
if
available):

 
the
exposed
population(
s)
 
potential
exposure
by
route
and
frequency
(
days/
yr)
 
aggregate
exposure
(
sum
total)
 
tasks,
processes,
activities
and
equipment
that
contribute
to
the
potential
exposure.

For
each
exposure
estimate,
provide:
 
the
year
to
which
the
estimate
pertains
(
the
most
recent
data
available
is
usually
most
appropriate):
 
the
cross­
reference
to
Format
B
or
C
in
which
the
estimate
was
reported.

44.
If
you
are
providing
qualitative
descriptions
(
e.
g.,
for
releases,
media
and
sources
without
numerical
release
estimates;
for
exposures,
routes
and
individual
activities
without
numerical
estimates),
attention
should
be
paid
to
thoroughness
and
clarity.
It
is
helpful
to
be
as
quantitative
and
precise
as
possible
(
i.
e.,
avoid
the
use
of
words
such
as
significant,
sufficient,
low,
negligible,
etc.,
unless
such
words
can
be
backed
up
by
explanatory
text.)

(
4)
Discussion
of
Factors
that
Decrease
or
Increase
Releases
and
Exposures
BACK
45.
Other
factors
are
described
that
may
affect
potential
releases
and
exposures.
Examples
of
helpful,
relevant
topics
to
include
if
available
:

 
physical
and
chemical
properties
of
the
chemical
that
have
a
significant
effect
on
exposure,
 
engineering
controls
(
e.
g.
ventilation
hoods,
air
pollution
control
equipment,
on­
or
off­
site
treatment)
 
administrative
policies
or
work
practice
controls
(
e.
g.
work
schedules,
cleaning,
maintenance
and
inspection
procedures)
 
personal
protective
equipment
(
e.
g.
gloves,
goggles,
respirators,
chemical
protective
clothing)
 
the
nature
of
the
wastewater
treatment
plant
(
biological,
chemical
etc)
with
information
on
its
effluent
flow
and
the
flow
of
surface
water
body
receiving
its
outflow.
 
any
international,
national,
regional,
or
local
regulations
that
apply
to
the
activities
at
the
facility
where
the
chemical
is
produced,
formulated,
or
used
industrially,
including
occupational
standards
(
e.
g.,
MAK,
PEL,
STEL,
TLV)
and
environmental
standards.

(
5)
Environmental
Exposure
BACK
46.
Information
on
any
discharges
associated
with
the
process
are
described,
including
if
available
:

 
direct
or
indirect
discharge
rate
(
L/
d),
 
the
parameters
of
any
treatment
processes,
including
if
available
flow
rate
(
L/
d),
process
type,
influent
and
effluent
concentrations,
removal
rate
of
the
substance,
biodegradation
removal
rate,
sorption
to
sludge,
sludge
disposal
information
and
dilution
factor
in
the
receiving
water.
 
parameters
relative
to
air
discharges
and
environmental
fate,
if
appropriate.
ENV/
JM/
MONO(
2003)
16
28
(
6)
Information
Not
Included
and
Rationale
BACK
47.
This
element
provides
an
opportunity
to
briefly
identify
and
explain
why
relevant
point
source,
exposed
population,
or
monitoring
data,
known
to
the
submitter,
is
not
included.
For
example,
although
a
submitter
may
possess
data
covering
years
of
monitoring,
the
precision
may
be
lacking
due
to
limits
of
the
methodology
or
equipment
used.
Therefore,
the
submitter
could
instead
provide
modeling
data
for
the
scenario.
A
simple
explanation
letting
the
reader
know
why
one
data
set
was
presented
over
the
other
should
be
provided.
In
another
example,
the
protection
of
proprietary
information
may
prevent
the
disclosure
of
company
or
site­
specific
information.
The
proprietary
information
may
be
aggregated
to
avoid
disclosure,
which
can
be
explained
in
one
or
two
sentences.

(
7)
Remarks
BACK
48.
Use
this
area
to
include
any
relevant
information
not
included
elsewhere
in
the
format.

Private/
Consumer
Use
(
8)
Function/
Product
Use
Category
Description
BACK
49.
For
chemicals
with
private
(
consumer)
uses,
identify
(
if
available):

 
the
product
categories
where
the
chemical
is
used,
 
the
function
of
the
substance
in
the
products,
 
the
physical
form
of
the
products,
and,
 
the
concentration
of
the
substance
in
the
product
50.
When
characterizing
consumer
uses
and
scenarios,
it
is
important
to
understand
the
releases
and
exposures
for
each
product
category
in
which
the
chemical
is
used.
The
following
questions
can
help
in
determining
additional
points
that
might
be
addressed
for
different
product
categories
and
are
especially
useful
in
developing
estimates
of
exposure
using
Format
B:
Monitoring
or
Format
C:
Modeling:

a.
How
frequently
is
each
private
and/
or
consumer
product
used?
b.
What
is
the
duration
of
use?
c.
How
much
of
the
product
is
used?
d.
Is
the
product
used
"
neat"
or
diluted?
If
diluted,
what
is
the
likely
use
concentration?
e.
Who
are
the
potentially
directly
exposed
populations
during
use
and
who
are
the
potentially
directly
exposed
populations
after
use?
Adults?
Children
(
ages)?
Infants?
Prenatal
exposures
to
children?
f.
What
are
the
activities
associated
with
the
exposures?
g.
What
are
the
likely
locations
of
exposure?
h.
Is
the
private
(
consumer)
product
likely
to
leave
residuals
after
use?
i.
What
are
the
likely
disposal
scenarios
for
the
product?
j.
Who
are
the
potentially
indirectly
exposed
populations
from
release
to
the
environment?
Adults?
Children
(
ages)?
Prenatal
exposures
to
children?
Ecological
exposures?

(
9)
General
Description
of
Direct
Human
Exposures
to
Consumer
Products
and
of
Potential
Releases
to
the
Environment
Leading
to
Ecological
Exposures
and
Indirect
Human
Exposures
Direct
Human
Exposures
BACK
ENV/
JM/
MONO(
2003)
16
29
51.
a)
Exposures:
Potential
human
exposures
from
consumer
uses
are
described.
This
may
cover
if
available,
for
each
consumer
product/
consumer
population
combination
listed
above
the
direct
exposure
to
the
chemical
by
route
of
exposure
and
the
exposure
frequencies
(
days/
yr)

Specify
the
units
(
e.
g.,
mg/
m3,
ppm,
mg/
day,
mg/
kg/
day,
etc.)
used
for
any
quantitative
value
and
the
year
that
is
covered
if
relevant.
Where
relevant,
provide
the
cross­
references
to
a
Format
B
or
Format
C.
It
is
helpful
to
be
as
quantitative
and
precise
as
possible
(
i.
e.,
avoid
the
use
of
words
such
as
significant,
sufficient,
low,
negligible,
etc.,
unless
such
words
can
be
backed
up
by
explanatory
text.)

Potential
Releases
to
the
Environment
leading
to
Ecological
and
Indirect
Human
Exposures
BACK
52.
b)
Releases:
Releases
are
described
and
cross
referenced
to
related
Format
B
and
C
estimates.

The
summary
identifies
all
likely
release
scenarios
from
consumer
products,
the
likely
receiving
media,
and
whether
the
release
would
be
periodic,
accidental
or
expected.
It
also
includes,
if
available:

 
each
medium
to
which
one
or
more
releases
occur
from
the
consumer
use
of
the
chemical,
 
the
release
rates
(
releases
to
surface
water
or
to
publicly
owned
treatment
works,
as
air
releases
or
emissions,
to
landfill),
 
the
media
concentrations,
and
 
indirect
exposures
via
the
environment
(
inhalation
exposures,
dermal
exposures,
drinking
water,
etc.)

It
is
helpful
to
be
as
quantitative
and
precise
as
possible
(
i.
e.,
avoid
the
use
of
words
such
as
significant,
sufficient,
low,
negligible,
etc.,
unless
such
words
can
be
backed
up
by
explanatory
text.)
It
may
be
helpful
to
describe
if
the
chemical
is
directly
released
in
the
media
(
emission
to
surface/
sea
water
or
air
without
treatment)
or
if
there
treatment
of
the
chemical
(
wastewater
treatment
plant,
etc.)
Specify
the
units
in
either
in
pounds
or
kilograms
and
maintain
the
same
units
throughout
the
summary
for
any
quantitative
value
and
the
year
that
is
covered
if
relevant.

(
10)
Discussion
of
Factors
that
Decrease
or
Increase
Releases
and
Exposures
BACK
53.
Other
factors
are
described
that
may
affect
potential
releases
and
exposures.
Examples
of
helpful,
relevant
topics
to
include
if
available
:

 
physical
and
chemical
properties
of
the
chemical,
 
whether
product
packaging,
labelling
or
use
instructions
are
likely
to
reduce
consumer
exposure
 
whether
ventilation
likely
to
be
in
place
during
the
use
 
whether
consumers
using
the
product
likely
to
wear
any
personal
protective
equipment
like
gloves
 
the
likely
nature
of
waste
disposal
(
11)
Remarks
BACK
54.
Use
this
field
to
include
any
relevant
information
not
included
elsewhere
in
the
format.

VII.
Unassociated
Format
B
and/
or
Format
C
(
1)
Notes
and
Remarks
on
Unassociated
Format
B
and/
or
Format
C
BACK
55.
If
one
or
more
Format
B
or
Format
C
cannot
be
linked
to
a
particular
production,
industrial
use,
ENV/
JM/
MONO(
2003)
16
30
commercial
use,
or
consumer
use,
provide
here
a
discussion
and
relevant
citations,
resources,
references,
etc.
(
e.
g.
national
biomonitoring
or
environmental
monitoring
studies
such
as
NHANES,
MOE,
USGS,
provides
results
that,
while
useful
for
exposure
assessments,
cannot
generally
be
related
back
to
a
specific
activity.)

VIII.
References
Format
A
References
BACK
56.
This
field
is
for
any
relevant
citations,
resources,
and
references.
ENV/
JM/
MONO(
2003)
16
31
Format
B:
Monitoring
Evaluation
­
Instructions
for
Completing
the
Format.
BACK
57.
The
monitoring
evaluation
format
is
to
be
used
to
provide
summary
information
from
monitoring
studies
for
the
chemical.
The
term
monitoring
covers
studies
in
which
data
are
the
result
of
measurements
of
the
chemical
in
environmental
media
(
e.
g.,
outdoor
air,
indoor
air,
surface
water,
soil,
etc.)
or
a
particular
exposure
scenario,
such
as
inhalation
or
dermal
exposure
monitoring.
It
also
includes
biomonitoring
data.
The
fields
are
flexible
to
be
able
to
include
monitoring
in
any
type
of
medium,
including
simple
environmental
matrices
such
as
air
and
water,
or
complex
biological
matrices
like
blood,
urine
or
tissue.
When
estimates
of
environmental
releases
or
exposures
are
based
on
a
monitoring
study,
the
monitoring
evaluations
format
maybe
used
to
describe
the
data
from
that
study.

Report
Title
58.
This
field
is
for
entering
the
title
of
the
overall
report,
the
same
as
that
used
in
the
associated
Format
A.

I.
Identification
Information
(
1)
Study
Title
59.
This
field
is
for
entering
a
brief
title
that
describes
the
study
(
2)
Activity
Associated
with
Monitoring
Information
BACK
60.
This
field
is
for
entering
the
appropriate
Format
A,
section
IV
number
to
which
this
release,
environmental
concentration,
or
exposure
(
or
intake
or
dose)
data
applies,
and
the
associated
description
from
that
section
(
i.
e.
the
cross­
reference
in
the
General
Description
of
Potential
Releases
and
Exposures
where
some
descriptions
could
include
general
environmental
monitoring,
worker
exposure
monitoring
for
production,
drinking
water
monitoring,
water
release
estimate
from
production,
etc.)

II.
Monitoring
Study
Design
and
Description
of
Scenario
Monitored
(
1)
Monitoring
Study
Objective
and
Scenario
Description
BACK
61.
In
this
section,
describe
the
general
scope
and
objectives
of
the
monitoring
study.
This
section
also
provides
you
with
an
opportunity
to
describe
why
the
data
are
relevant.

62.
Describe
the
objectives
of
the
monitoring
study
to
which
the
results
apply
(
e.
g.
to
determine
estimates
of
average
and
high
end
release
or
exposures
to
the
population
of
interest;
for
exploratory
purposes
relating
to
the
population,
release,
or
chemical
of
interest;
as
surrogate
monitoring
data
that
did
not
directly
study
the
release,
population,
or
chemical
of
interest;
of
an
unknown
study
objective;
etc.).

63.
Listed
below
are
statements
that
you
might
use
to
describe
the
objectives
of
a
study:

 
Monitoring
data
for
the
chemical
of
interest
collected
using
a
study
design
that
will
permit
estimates
of
average
and
high­
end
release
or
exposure
to
the
population
of
interest.
 
Monitoring
data
for
the
chemical
of
interest
collected
on
the
release
or
population
of
interest
for
exploratory
purposes
but
not
for
estimating
average
or
high­
end
releases
or
exposures.
ENV/
JM/
MONO(
2003)
16
32
 
Surrogate
monitoring
data
(
i.
e.
data
not
collected
directly
on
the
release
or
population
or
chemical
of
interest)
but
for
a
similar
exposure
scenario.
 
Monitoring
data
that
lack
documentation
on
study
objective
and/
or
design.

64.
Briefly
describe
the
scenario
monitored,
location,
dates,
and
study
design.
Depending
on
the
scenario,
other
relevant
information
could
include:

 
frequency
of
release
or
exposure,
 
amount
of
chemical
/
product
used,
 
physical
form
in
which
the
chemical
/
product
was
used,
 
information
on
existing
exposure
controls,
etc.),
 
whether
the
study
assessed
acute
or
chronic
exposures,
 
whether
typical
or
conservative
(
i.
e.
protective)
releases
or
exposures
were
estimated,
and,
 
the
specific
release
source
or
population
(
e.
g.
occupational
job
descriptions
or
consumer)
that
was
monitored
and
activities
performed
during
monitoring,
if
applicable.

III.
Sampling
and
Analytical
Methods
(
1)
Media
Sampled
BACK
65.
This
section
should
be
used
to
describe
the
media
that
was
sampled
in
the
monitoring
study
[
e.
g.
personal
inhalation
monitoring
(
air
sampled
from
the
breathing
zone
of
a
worker
or
consumer),
personal
dermal
exposure
monitoring
(
a
wipe
sample
taken
from
the
skin
or
gloves
of
a
worker
or
consumer),
biomonitoring
(
personal
blood,
urine
or
tissue
sampling),
or
a
general
sample
of
air,
water,
wastewater,
groundwater,
soil,
clothing,
or
work
surfaces.]

(
2)
Sampling
BACK
66.
Provide
information
about
the
method
used
to
collect
the
samples
for
the
study.
Include
other
relevant
information
such
as:

 
the
dates
in
which
samples
were
obtained,
 
the
duration
of
the
study,
 
number
of
samples,
 
sampling
periods,
 
locations
of
sampling,
 
sample
storage
and
preservation,
 
information
on
monitoring
equipment
instrumentation,
documentation
and
variations
from
established
procedures.

(
3)
Method/
Procedure
BACK
67.
Describe
the
analytical
method
used
to
analyze
the
samples
collected,
including
any
number
or
standard
affiliation
and
associated
documentation.
Include
information
on
validation
by
an
independent
body
(
e.
g.
ASTM
standard
method
xxxx,
NIOSH
method
yyyy),
or
an
individual
company
(
e.
g.
method
number
1234
developed
by
company
ABC).
Include
the
limit
of
detection
and
the
limit
of
quantification
of
the
chemical
with
the
method
and
any
evaluation
of
sampling
and
measurements
parameters
(
e.
g.
overall
uncertainty,
overall
precision,
overall
bias,
accuracy,
recovery
from
collection
media,
capacity
of
collection
media,
stability
of
collected
analyte(
s),
sampling
interferences,
measurement
range,
measurement
precision,
measurement
interferences).
ENV/
JM/
MONO(
2003)
16
33
68.
Listed
below
are
statements
that
you
may
wish
to
use
to
describe
the
methods
or
procedures
of
a
study:

 
Monitoring
data
collected
and
analyzed
using
sampling
and
analytical
chemistry
methods
that
have
been
validated
and
accepted
by
an
independent
body
(
e.
g.
ASTM,
NIOSH,
etc.).
 
Monitoring
data
collected
and
analyzed
using
well­
documented
sampling
and
analytical
chemistry
methods.
 
Monitoring
data
collection
and
analysis
documentation
is
not
available.

IV.
Results
and
Reliability
Description
(
1)
Results
BACK
69.
Summarize
the
results
of
a
monitoring
study.
The
numerical
results
and
units
should
be
provided
and
characterized
(
e.
g.
time­
weighted
averages,
representative/
typical
conditions,
worst­
case
scenario,
conservative,
grab
sample,
daily
average
concentration,
etc.)

70.
Unless
you
have
very
few
data
for
a
particular
exposure
scenario,
it
is
likely
that
you
will
need
to
use
some
form
of
statistics
to
summarise
them.
It
is
suggested
that
the
median
and
percentiles
such
as
the
90th
and
95th
be
used
as
measures
of
location,
confidence
intervals
around
these
be
used
to
indicate
their
uncertainty.
These
statistics
are
nonparametric,
i.
e.,
they
do
not
rely
on
any
assumptions
about
whether
data
are
normal,
lognormal
or
are
from
any
other
skewed
distribution
and
are
appropriate
for
all
data
sets.
More
conventional
statistics
(
means,
geometric
means,
standard
deviations,
geometric
standard
deviations
etc)
are
inappropriate
unless
the
assumptions
about
a
distribution
can
be
tested.
Remember
though,
it
can
take
a
large
number
of
data
points
(
specific
references)
to
test
that
your
data
fits
a
particular
distribution
at
a
reasonable
level
of
confidence.
The
use
of
inappropriate
statistics
can
lead
to
incorrect
conclusions
being
drawn
about
exposures.
So,
whatever
statistics
are
selected,
it
would
be
helpful
to
provide
a
brief
rationale
for
your
choice.
Some
helpful
literature
on
summary
statistics
are
included
in
the
Annex
3
references.

71.
Where
there
is
a
need
to
provide
integrated
data,
for
example
if
there
is
a
desire
to
predict
exposed
dose,
then
the
supporting
equations
should
be
given
and
reference
made
to
the
sources
of
input
parameters
(
see
Annex
3).
There
are
a
variety
of
equations
and
methods
that
may
be
used
for
providing
estimates
of
exposure,
such
as
an
equation
for
estimating
ppm
x
hours
of
exposure
or
selection
of
an
estimate
of
peak
exposure
concentration
over
a
specified
time
interval.
In
exposure
assessment
equations
for
providing
estimates
of
dose
and
intake
such
as
average
daily
dose
(
ADD),
lifetime
average
daily
doses
(
LADD),
average
daily
intake,
etc.,
are
also
used.
The
data
provided
by
the
monitoring
study
is
one
of
the
inputs.
Other
inputs
could
include
parameters
such
as
breathing
rate,
duration
of
exposure,
body
weight,
skin
surface
area
in
contact
with
a
contaminant,
etc.,
and
these
parameters
would
depend
upon
the
equation
used.
For
information
on
the
definitions
and
equations
for
these
and
other
estimates
of
exposure,
dose
and
intake,
Annex
3
may
be
a
valuable
resource.
If
biological
monitoring
data
are
being
used
to
reconstruct
a
dose,
summarize
how
this
was
done
and
what
assumptions
were
made.

72.
Also
describe
here
any
relevant
characteristics
of
the
exposed
population
that
is
being
assessed
(
e.
g.
size
of
the
assessed
population,
age
of
the
assessed
population,
location
of
the
assessed
population
if
that
is
relevant,).
Remember
that
when
exposure
is
characterized
as
being
average,
conservative,
etc.,
that
characterization
applies
to
a
specific
population
and
to
the
type
of
exposure
being
estimated
(
i.
e.
acute
or
chronic
exposure).

73.
If
data
from
two
or
more
differently
exposed
populations
are
combined,
this
should
be
indicated
and
a
rationale
provided.
ENV/
JM/
MONO(
2003)
16
34
(
2)
Reliability
Score
BACK
74.
Describe
the
reliability
of
each
release
or
exposure
estimate
in
the
Results
section
above
by
selecting
the
appropriate
reliability
score
below,
with
explanation
of
the
reason
why
this
score
was
selected.

­
1
valid
without
restrictions
All
the
following
bullet
points
should
be
met.
 
a
valid
analytical
method
including
quality
control
was
used
for
the
intended
matrix
(
water,
sediment,
soil,
sludge,
air
etc)
and
which
is
sensitive
enough
for
the
intended
purpose
 
Representative
data
including
quality
controls
are
available
for
the
population
or
scenario
of
interest
to
sufficiently
describe
the
releases
or
exposures
 
measured
data
are
statistically
analysed,
outliers
identified
and
eliminated
 
The
study
design
used
to
collect
the
data
is
appropriate
and
well
documented
(
e.
g.
sampling
location,
description
of
matrix,
sampling
period
etc)

­
2
valid
with
restrictions
All
the
following
bullet
points
should
be
met.
 
a
valid
analytical
method
including
quality
control
was
used
for
the
intended
matrix
(
water,
sediment,
soil,
sludge,
air
etc)
and
which
is
sensitive
enough
for
the
intended
purpose
 
Representative
data
including
quality
controls
are
available
for
the
population
or
scenario
of
interest
to
sufficiently
describe
the
releases
or
exposures
 
The
study
design
used
to
collect
the
data
is
appropriate
and
well
documented
(
e.
g.
sampling
location,
description
of
matrix,
sampling
period
etc)

­
3
not
valid
 
measurements
are
available;
however
insufficient
confidence
can
be
invested
in
the
measurements
(
e.
g.
no
information
is
available
on
the
sampling
or
analytical
conditions)
OR
 
The
measurements
are
not
representative
of
the
population
or
scenario
of
interest
­
4
not
assignable
 
measurements
are
available,
but
without
supporting
documentation
so
that
for
the
time
being
the
reliability
cannot
be
judged
(
3)
Remarks
BACK
75.
Include
any
relevant
citations,
resources
used,
applicable
study
notes,
etc.
for
the
monitoring
study
and
any
associated
release
or
exposure
estimates.

V.
References
(
1)
Format
B
References
BACK
76.
This
field
is
for
any
relevant
citations,
resources,
and
references.
ENV/
JM/
MONO(
2003)
16
35
Format
C:
Modelling
Evaluation
 
Instructions
for
Completing
the
Format
BACK
77.
This
format
is
to
be
used
when
modeling
is
done
to
estimate
exposures
(
or
intakes
or
doses)
or
to
estimate
releases
or
environmental
concentrations,
which
can
then
be
used
to
estimate
exposure.
Although
the
word
model
is
often
associated
with
scientific
computer
software
applications,
it
can
also
be
used
to
describe
one
or
more
algorithms
or
mathematical
equations.
Models
can
be
used
to
make
estimates
of
human
exposure
directly
or
estimates
of
chemical
release
or
chemical
concentration
in
an
environmental
media
which
can
then
be
used
to
make
subsequent
estimates
of
exposure.
It
is
also
true
that
estimates
of
exposure
(
i.
e.
concentration
x
duration
of
contact)
and
dose
(
e.
g.
daily
intake,
absorbed
dose)
are
usually
generated
using
"
models."

78.
Scientists
routinely
use
data
from
monitoring
studies
to
validate
exposure
models,
although
not
necessarily
for
the
specific
chemical
of
interest.
Monitoring
data
can
also
be
used
as
an
input
for
some
models.
There
are
also
models
that
use
the
outputs
of
other
models
as
inputs.

Report
Title
79.
This
field
is
for
entering
the
title
of
the
overall
report,
the
same
as
that
used
in
the
associated
Format
A.

I.
Identification
Information
(
1)
Study
Title
80.
This
field
is
for
entering
a
brief
title
that
describes
the
study
(
2)
Activity
Associated
with
Modeling
Information
BACK
81.
This
field
is
for
entering
the
appropriate
Format
A,
section
IV
number
to
which
this
release
or
exposure
modelling
data
applies
and
the
associated
description
from
that
section
(
i.
e.,
the
cross­
reference
in
the
General
Description
of
Potential
Releases
and
Exposures
where
some
descriptions
could
include
general
environmental
modelling,
industrial
use
#
2
worker
inhalation
exposure
modelling,
modelling
for
production
releases
from
source
x,
etc.)

II.
Modeling
Objective
and
Description
of
Modeled
Scenario
(
1)
Modeling
Study
Objective
and
Scenario
Description
BACK
82.
This
field
is
for
explaining
the
general
scope
and
objectives
of
the
study;
for
instance,
to
state
whether
the
objective
was
to
provide
a
conservative
estimate
of
release
or
exposure,
a
representative
estimate
of
release
or
exposure
or
some
other
kind
of
estimate
of
release
or
exposure.
This
field
is
also
for
identifying
the
population
being
assessed
and
whether
the
study
is
intended
to
estimate
acute
or
chronic
exposures,
or
both.
When
using
a
model
to
estimate
environmental
media
concentrations
and
exposures,
it
is
common
to
do
these
at
the
same
time
and
as
part
of
the
same
study.
In
this
case
it
is
not
necessary
to
separately
discuss
the
objective
for
estimating
the
media
concentration
and
the
objective
for
the
exposure
assessment.
ENV/
JM/
MONO(
2003)
16
36
83.
This
field
is
also
to
be
used
to
describe
the
scenario
being
modelled,
which
includes
information
like
duration
(
hours/
day)
and
frequency
(
days/
yr)
of
release
or
exposure,
amount
of
chemical/
product
used,
physical
form
in
which
the
chemical/
product
was
used,
information
on
exposure
controls
and
whether
the
modelling
assesses
acute
or
chronic
exposures.
Include
information
on
whether
it
was
designed
to
estimate
typical
or
conservative
(
i.
e.
protective)
releases
or
exposures,
and
the
basis
for
the
characterization.

84.
Identify
the
specific
population
(
e.
g.
worker
job
descriptions
or
consumer)
and
activities
performed,
if
applicable,
for
which
the
modelling
is
being
done.

III.
Description
of
Model
and
Model
Validation
(
1)
Tool
or
Model
BACK
85.
This
field
is
for
providing
the
name
of
the
tool
or
model,
including
a
brief
description
of
the
model
algorithm
(
if
appropriate),
and
its
applicability
to
this
assessment
and
the
date(
s)
on
which
the
model
was
run.
If
applicable,
provide
the
version
number
of
the
model.
Note
that
simple,
first
principle
equations
are
often
used,
especially
in
screening
level
assessments
which
err
on
the
side
of
being
protective.
In
that
case,
the
inputs,
outputs,
exposure
factors,
and
other
relevant
information
will
be
important
for
transparency.

(
2)
Validation/
Peer
Review
BACK
Note
that
the
information
in
sections
(
2)
and
(
3)
need
only
be
provided
one
time
if
the
same
model
is
used
for
multiple
estimates.

86.
This
field
is
for
describing
any
model
evaluations
and/
or
peer
reviews
that
have
been
performed
or
for
providing
citations
of
such
evaluations/
peer
reviews.
If
the
model
has
undergone
an
evaluation,
information
may
be
provided
on
how
the
model
performed
and
some
background
information
about
the
evaluation
(
i.
e.,
how
input
data
were
selected,
was
the
model
validated
against
field
observations
or
against
other
models,
what
type
of
expert(
s)
conducted
the
peer
review?
etc.).
The
extent
to
which
a
model
is
accepted
for
by
the
scientific
and
regulatory
community
may
be
noted.
Example
summary
statements
might
include:

 
The
model
has
been
validated
with
monitoring
data
that
is
directly
relevant
for
the
scenario
of
interest.
 
The
model
has
been
evaluated
with
monitoring
data
but
it
has
not
been
formally
validated.
 
The
model
has
not
been
validated
or
evaluated
with
monitoring
data.
 
The
model
has
been
through
a
formal
peer
review
process.
 
The
model
has
been
informally
peer
reviewed.
 
The
model
has
not
had
any
peer
review.
 
The
model
has
(
wide,
limited,
no)
acceptance
among
the
scientific
and
regulatory
community.

(
3)
Availability
and
Documentation
BACK
87.
If
applicable,
provide
information
on
how
to
obtain
the
model
and
documentation,
and
references
to
evaluations
and
reviews
of
the
model
that
are
not
listed
elsewhere.
For
example,
you
may
provide
information
on
how
to
obtain
the
model
(
e.
g.
private
model
with
limited
release,
model
with
closed
code
available
for
purchase,
model
available
at
low
or
no
cost
with
code
available
for
inspection,
model
available
at
low
or
no
cost
with
code
available
for
inspection
and
modification,
model
available
in
ENV/
JM/
MONO(
2003)
16
37
publication
x,
etc.),
related
guidance
documents,
evaluations
and
reviews
that
are
not
part
of
a
peer
review
process,
and
any
other
information
that
may
be
relevant.

IV.
Inputs,
Outputs,
and
Reliability
Description
(
1)
Media
Modeled
BACK
88.
Describe
the
type
of
medium
or
matrix
modeled
(
e.
g.,
soil,
clothing
or
patches
of
cloth)
and
how
the
medium
can
affect
the
potential
for
exposure
(
e.
g.
transport
through
soil.)
Models
can,
and
have
been,
developed
to
include
specifics
on
the
type
of
medium
or
matrix
in
which
the
chemical
of
interest
is
contained.
Various
media
can
include:
air,
water,
soil,
clothing
or
patches
of
cloth,
work
surfaces,
specific
solid
materials,
blood,
tissue,
and
many
others.
You
may
also
wish
to
include
how
the
medium
can
affect
the
potential
for
exposure
to
the
chemical
of
interest
(
e.
g.
transport
through
soil,
diffusion
through
liquid,
leaching
from
a
solid).

(
2)
Inputs
BACK
89.
The
values
of
key
input
parameters
should
be
provided.
If
the
model's
default
values
have
been
changed,
a
reason
should
be
provided.
Many
models
use
certain
assumptions,
which
can
appear
as
default
values
in
specific
equations.
Other
models
do
not
use
defaults
but
require
the
user
to
supply
all
of
the
inputs.
In
this
field,
list
the
key
input
values
and
units,
and
list
any
changes
to
the
defaults.
Also
provide
here
your
rationale
for
changing
default
values
(
e.
g.
direct
measurements
of
habits
and
practices
for
the
situation
of
interest).
Some
of
the
key
inputs
that
are
often
encountered
when
performing
a
modeling
study
are:
sources
(
e.
g.
release
rates
into
the
environment,
the
days
of
release,
receiving
stream
flows,
house
volumes
and
air
exchange
rates,
etc.);
approximate
percentage
of
aggregate
product
volume
that
goes
into
a
specific
product
or
use;
physical
form
of
the
chemical;
likely
route
of
exposure;
amount
of
product
used
per
application,
and
the
concentration
of
the
chemical
being
studied;
known
or
recommended
dilution
ratios
for
use;
disposal
routes;
and
others,
depending
on
the
model.
You
may
choose
to
use
certain
inputs
in
the
areas
described
above,
or
may
elect
to
use
the
model's
default
values.

90.
Listed
below
are
statements
that
you
may
wish
to
include
to
describe
various
inputs
used
in
a
modeling
study:

 
measured
site
or
scenario
specific
value.
 
estimated
site
or
scenario
specific
value.
 
generic
conservative
default
value.

(
3)
Estimated
Model
Outputs
BACK
91.
This
section
is
for
providing
modeling
results
and
the
exposed
population
(
e.
g.
size
of
the
assessed
population,
age
of
the
assessed
population,
location
of
the
assessed
population,
if
that
is
relevant)
associated
with
each
modeled
value;
for
characterizing
the
results
(
i.
e.,
average,
conservative,
etc.),
and
providing
a
basis
for
the
characterization.
Take
care
to
ensure
that:
appropriate
units
are
provided,
dimensions
are
correct,
conversion
factors
are
used
correctly,
non­
dimensional
quantities
are
correctly
expressed,
and
the
number
of
significant
figures
given
are
correct.
When
summarizing
the
results
of
the
model
estimation
of
environmental
media
concentration,
use
this
field
to
describe
any
equations
used
to
estimate
exposures
(
or
intake,
or
dose)
and
the
values
and
sources
of
the
inputs
to
the
equation.
The
numerical
results,
including
the
units,
should
be
provided
and
characterized
(
e.
g.
average,
conservative,
etc.),
along
with
the
basis
for
the
characterization
(
e.
g.
the
inputs
are
intended
to
provide
an
estimate
of
average
(
acute
or
chronic)
exposure,
intake,
or
dose
to
the
population
being
assessed.)
ENV/
JM/
MONO(
2003)
16
38
92.
There
are
various
equations
and
methods
that
may
be
used
for
providing
estimates
of
exposure,
such
as
an
equation
for
estimating
ppm
x
hours
of
exposure
or
selection
of
an
estimate
of
peak
exposure
concentration
over
a
specified
time
interval.
In
exposure
assessment
it
is
also
common
to
use
equations
for
providing
estimates
of
dose
and
intake
such
as
average
daily
dose
(
ADD),
lifetime
average
daily
doses
(
LADD),
average
daily
intake,
etc.
The
output
provided
by
the
model
for
an
environmental
media
concentration
may
be
an
input
to
another
model.
Other
inputs
could
include
parameters
such
as
breathing
rate,
duration
of
exposure,
body
weight,
skin
surface
area
in
contact
with
a
contaminant,
etc.,
and
these
parameters
would
depend
upon
the
equation
used.
For
information
on
the
definitions
and
equations
for
these
and
other
estimates
of
exposure,
dose
and
intake,
Annex
3
is
a
valuable
resource.

93.
If
data
from
two
or
more
differently
exposed
populations
are
combined,
this
should
be
indicated
and
a
rationale
provided.

(
4)
Reliability
Score
BACK
94.
Determine
the
reliability
of
each
release,
environmental
concentration,
or
exposure
(
or
intake
or
dose)
estimate
in
the
Results
section
(
C.
IV.
3.)
by
selecting
the
most
appropriate
reliability
score,
with
explanation
of
why
this
score
was
selected.

­
1
valid
without
restrictions
The
first
or
second
bullet
point
should
be
met.
The
third
bullet
point
should
also
be
met.
 
the
model
has
been
validated
for
the
scenario
of
interest,
peer
reviewed
and
well
documented.
Sufficient
experience
demonstrates
its
applicability
for
the
intended
use
in
exposure
assessment
and
ultimately
risk
characterization.
;
OR
 
model
is
sufficiently
conservative,
has
undergone
peer
review
and
is
generally
accepted
by
authorities
AND
 
exposure
modelling
for
the
given
substance
falls
into
the
applicability
domain
of
the
model
and
appropriate
inputs
are
used
­
2
valid
with
restrictions
The
first
or
second
bullet
point
should
be
met.
The
third
bullet
point
should
also
be
met.
 
The
model
is
accepted
for
the
current
purposes
as
a
result
of
wide
experience
by
scientists
from
the
regulatory,
industrial
and
academic
community
OR
 
model
is
sufficiently
conservative,
has
undergone
peer
review
or
is
generally
accepted
by
authorities
AND
 
modelling
for
the
given
substance
falls
into
the
applicability
domain
of
the
model
and
appropriate
inputs
are
used
­
3
not
valid
 
model
has
not
been
confirmed
by
sufficient
case
studies
or
case
studies
suggest
that
it
is
not
reliably
applicable;
application
of
the
model
would
deliver
results
which
would
be
"
not
valid"
OR
 
model
is
accepted
but
the
modelling
for
the
given
substance
falls
out
of
the
applicability
domain
of
the
model
and
therefore
the
result
would
be
"
not
valid"
OR
 
model
is
accepted
but
the
inputs
are
not
appropriate
or
well
documented
and
therefore
the
result
would
be
"
not
valid"
ENV/
JM/
MONO(
2003)
16
39
­
4
not
assignable
 
model
and/
or
input
values
are
not
described
or
documented
sufficiently
to
judge
if
it
can
be
applied
for
this
scenario.
Reliability
of
the
results
would
be
"
not
assignable".
Use
of
this
model
cannot
provide
useful
results
for
exposure
assessment
and
risk
characterization
until
the
missing
facts
on
the
model
are
made
available.

(
5)
Remarks
BACK
94.
Include
any
relevant
citations,
resources
used,
applicable
study
notes,
etc.
for
the
modelling
study
and
any
associated
release
or
exposure
estimates.

V.
References
(
1)
Format
C
References
BACK
95.
This
field
is
for
any
relevant
citations,
resources,
and
references.
ENV/
JM/
MONO(
2003)
16
40
ANNEX
1:
INFORMATION
ON
PHYSICAL
AND
CHEMICAL
PROPERTIES,
EXPOSURE
LIMITS
This
annex
provides
a
format
that
can
be
used
when
summary
information
on
physical,
chemical
or
hazard
properties
is
to
be
reported
in
conjunction
together
with
the
Formats
A­
C.
Alternatively,
the
Full
SIDS
Summary
Format
and
SIAM
dataset
may
be
used.

MEASURED/
CALCULATED
PROTOCOL/
SPECIES
DATA
PHYSICAL­
CHEMICAL
Molecular
weight
Physical
form
Melting
Point
°
C
Boiling
Point
°
C
(
at
kPa)

Density
kg/
m3
Vapour
Pressure
kPa
at
°
C
Henry's
Law
constant
Partition
Coefficient
(
Log
Pow)

Water
Solubility
mg/
l
at
°
C
pH
at
°
C
pKa
Oxidation:
Reduction
Potential
mV
ENVIRONMENTAL
FATE
AND
PATHWAY
Photodegradation
In
air
t1/
2
=
hour
Stability
in
Water
t1/
2
=
min
Adsorption/
desorption
to
soil
at
°
C
Calculated
distribution
between
environmental
compartments
Calculated
(
Fugacity
Level
1
type)
In
Air
%
In
Water
%
In
Sediment
%
In
Soil
%
In
Biota
%

Bioconcentration
Factor
Biodegradation
EXPOSURE
LIMITS
Occupational
Exposure
Limits
ppm
or
mg/
m3
Others
ENV/
JM/
MONO(
2003)
16
41
ANNEX
2:
GLOSSARY
OF
TERMINOLOGY
This
annex
provides
definitions
of
key
terms
used
in
this
document.
These
definitions
originate
from
OECD
(
2003),
"
Descriptions
of
Selected
Key
Generic
Terms
Used
in
Chemical
Hazard/
Risk
Assessment
 
Joint
OECD/
IPCS
Project
on
the
Harmonisation
of
Hazard/
Risk
Assessment
Terminology",
Testing
and
Assessment
Series
No.
44.

Term
Description
Analysis
Detailed
examination
of
anything
complex,
made
in
order
to
understand
its
nature
or
to
determine
its
essential
features.

Assessment
Evaluation
or
appraisal
of
an
analysis
of
facts
and
the
inference
of
possible
consequences
concerning
a
particular
object
or
process.

Concentration
Amount
of
a
material
or
agent
dissolved
or
contained
in
unit
quantity
in
a
given
medium
or
system.

Dose
Total
amount
of
an
agent
administered
to,
taken
up
or
absorbed
by
an
organism,
system
or
(
sub)
population.

Effect
Change
in
the
state
or
dynamics
of
an
organism,
system
or
(
sub)
population
caused
by
the
exposure
to
an
agent.

Exposure
Concentration
or
amount
of
a
particular
agent
that
reaches
a
target
organism,
system
or
(
sub)
population
in
a
specific
frequency
for
a
defined
duration.

Exposure
Assessment
Evaluation
of
the
exposure
of
an
organism,
system
or
(
sub)
population
to
an
agent
(
including
its
derivatives).

Exposure
Scenario
A
set
of
conditions
or
assumptions
about
sources,
exposure
pathways,
amount
or
concentrations
of
agent(
s)
involved,
and
exposed
organism,
system
or
(
sub)
population
(
i.
e.
numbers,
characteristics,
habits)
used
to
aid
in
the
evaluation
and
quantification
of
exposure(
s)
in
a
given
situation.

Fate
Pattern
of
distribution
of
an
agent,
its
derivatives
or
metabolites
in
an
organism,
system,
compartment
or
(
sub)
population
of
concern
as
a
result
of
transport,
partitioning,
transformation
or
degradation.

Hazard
Inherent
property
of
an
agent
or
situation
having
the
potential
to
cause
adverse
effects
when
an
organism,
system
or
(
sub)
population
is
exposed
to
that
agent.

Hazard
Assessment
A
process
designed
to
determine
the
possible
adverse
effects
of
an
agent
or
situation
to
which
an
organism,
system
or
(
sub)
population
could
be
exposed.

The
process
includes
hazard
identification
and
hazard
characterization.
The
process
focuses
on
the
hazard
in
contrast
to
risk
assessment
where
exposure
assessment
is
a
distinct
additional
step.
ENV/
JM/
MONO(
2003)
16
42
Risk
The
probability
of
an
adverse
effect
in
an
organism,
system
or
(
sub)
population
caused
under
specified
circumstances
by
exposure
to
an
agent.

Risk
Characterization
The
qualitative
and,
wherever
possible,
quantitative
determination,
including
attendant
uncertainties,
of
the
probability
of
occurrence
of
known
and
potential
adverse
effects
of
an
agent
in
a
given
organism,
system
or
(
sub)
population,
under
defined
exposure
conditions.

Uncertainty
Imperfect
knowledge
concerning
the
present
or
future
state
of
an
organism,
system
or
(
sub)
population
under
consideration.

Validation
Process
by
which
the
reliability
and
relevance
of
a
particular
approach,
method,
process
or
assessment
is
established
for
a
defined
purpose.

Different
parties
define
"
Reliability"
as
establishing
the
reproducibility
of
the
outcome
of
the
approach,
method,
process
or
assessment
over
time.
"
Relevance"
is
defined
as
establishing
the
meaningfulness
and
usefulness
of
the
approach,
method,
process
or
assessment
for
the
defined
purpose.
ENV/
JM/
MONO(
2003)
16
43
ANNEX
3:
RESOURCES
Emission
Scenario
Documents:

OECD,
2001
Use
and
Release
of
Industrial
Chemicals,
OECD's
Database
on
Use
and
Release
of
Industrial
Chemicals
http://
webdomino1.
oecd.
org/
ehs/
urchem.
nsf
EU,
2003
EU
Technical
Guidance
Document
in
Support
of
Commission
Directive
93/
67/
EEC
on
Risk
Assessment
for
new
notified
substances,
Commission
Regulation
1488/
94/
EEC
for
existing
substances,
and
Directive
98/
8/
EC
of
the
European
Parliament
and
of
the
Council
concerning
the
placing
of
biocidal
products
on
the
market,
2003
Part
IV,
Emission
Scenario
Documents;
Source:
http://
ecb.
jrc.
it/
Documents/
TECHNICAL_
GUIDANCE_
DOCUMENT/
EDITION_
2/
tgdpart4_
2ed.
pdf
Exposure
Factors:

Canada,
1993
Reference
Values
for
Canadian
Populations,
May
1993
U.
S.
EPA,
1997
U.
S.
EPA/
ORD
Exposure
Factors
Handbook
(
1997);
www.
epa.
gov/
ncea/
exposfac.
htm
U.
S.
EPA,
2000
U.
S.
EPA/
ORD
Child­
Specific
Exposure
Factors
Handbook
(
External
Review
Draft
June
2000);
http://
cfpub.
epa.
gov/
ncea/
cfm/
recordisplay.
cfm?
deid=
55145
U.
S.
EPA,
1993
U.
S.
EPA/
ORD
Wildlife
Exposure
Factors
Handbook
(
1993)
http://
cfpub.
epa.
gov/
ncea/
cfm/
wefh.
cfm
U.
S.
EPA,
1999
U.
S.
EPA/
ORD
Sociodemographic
Data
Used
for
Identifying
Potentially
Highly
Exposed
Populations
(
1999);
http://
cfpub.
epa.
gov/
ncea/
cfm/
sociodeg.
cfm
U.
S.
EPA,
U.
S.
EPA/
ORD
Volatilization
Rates
from
Water
to
Indoor
Air
Phase
II
http://
cfpub.
epa.
gov/
ncea/
cfm/
volatiliz.
cfm
Ausschuss
für
Umwelthygiene
(
AUH)
(
1994)
Standards
zur
Expositionsabschätzung.
Arbeitsgemeinschaft
der
leitenden
Medizinalbeamtinnen
und
­
beamten
der
Länder,
Behörde
für
Arbeit,
Gesundheit
und
Soziales,
Hamburg,
1995.
Bremmer
HJ,
van
Veen
MP
(
2000)
Factsheet
allgemeen.
Randvoorwaarden
en
betrouwbarheid,
ventilatie
kammergroote,
lichamsoppervlak.
RIVM
report
612810009
ECETOC
Exposure
Factors
Sourcebook
for
European
Populations
(
with
focus
on
UK
Data)
ECETOC
Technical
Report
No.
79
Bremmer
HJ,
Van
Veen
MP
(
2000)
Factsheet
Verf.
Ten
behoeve
van
de
schatting
van
de
risico's
voor
de
consument.
RIVM
Report
No.
612810010
http://
www.
rivm.
nl/
bibliotheek/
rapporten/
612810010.
html
Bremmer
HJ,
Van
Veen
MP
(
2002)
Children's
Toys
Fact
Sheet.
To
assess
the
risks
for
the
consumer.
RIVM
Report
No.
612810012
http://
www.
rivm.
nl/
bibliotheek/
rapporten/
612810012.
html
AIHC
(
1994).
Exposure
Factors
Handbook,
Update.
American
Industrial
Health
Council
(
AIHC),
Washington,
DC
ENV/
JM/
MONO(
2003)
16
44
Summary
Statistics
Hoaglin
DC,
Mosteller
F,
Tukey
JW,
eds
Understanding
Robust
and
Exploratory
Data
Analysis,
John
Wiley
and
Sons,
Inc,
New
York,
NY,
USA,
1983
Sprent
P,
Smeeton
NC
Applied
Nonparametric
Statistical
Methods,
3rd
Edition,
Chapman
and
Hall,
CRC,
London,
2001
Sprent
P
Data
Driven
Statistical
Methods,
Chapman
and
Hall,
London,
1998
Hollander
M,
Wolfe
DA
Nonparametric
Statistical
Methods,
2nd
Edition,
John
Wiley
and
Sons,
Inc,
London,
1999
Hettmansperger
TP,
McKean
JW
Robust
Nonparametric
Statistical
Methods,
Arnold,
Hodder
Headline
Group,
London,
1998,
Chapter
1
Efron
B,
Tibshirani,
RJ
An
Introduction
to
the
Bootstrap,
Chapman
and
Hall,
London,
1993
Function/
Product
Use
Description
Environmental
Defense
Environmental
Defense
Fund
website
with
over
6,000
chemical
profiles
http://
www.
scorecard.
org/
chemical­
profiles/
ChemExpo
Profiles
of
industrial
chemicals
http://
www.
chemexpo.
com
SPIN
Database
Nordic
product
register
database
http://
www.
spin2000.
net/
spin.
html
Models:

Alliance
for
Chemical
Awareness
Alliance
for
Chemical
Awareness
website
http://
www.
chemicalawareness.
org
California
EPA,
1994
CalTox
(
TM),
Multimedia
Total
Exposure
Model
for
Hazardous
Waste
Sites,
California
EPA,
1994,
Version
1.5,
latest
version
2.3
http://
www.
dtsc.
ca.
gov/
ScienceTechnology/
ctox_
dwn.
html
ECETOC,
1992
ECETOC
Report
No.
50,
Estimating
Environmental
Concentrations
of
Chemicals
using
Fate
and
Exposure
Models,
November
1992,
ISSN­
0773­
8072­
50
ECETOC,
1994
ECETOC
Special
Report
No.
8,
HAZCHEM,
A
mathematical
model
for
use
in
Risk
Assessment
of
Substances,
October
1994,
ISSN
­
0773­
8072­
8
EUSES,
1997
EUSES,
European
Union
System
for
the
Evaluation
of
Substances,
Software
Version
1.01,
1997
http://
ecb.
jrc.
it/
existing­
chemicals/
OECD
,
1993a
Report
of
the
OECD
Workshop
on
the
Application
of
simple
models
for
Environmental
Exposure
Assessment,
1993,
OCDE/
GD
(
93)
127
http://
www.
oecd.
org/
env/
riskassessment
OECD,
1993b
OECD
Environment
Monographs,
No.
70,
Occupational
and
Consumer
Exposure
Assessments,
1993,
OCDE/
GD
(
93)
128
OECD,
2003
OECD
Database
on
Models
http://
webdomino1.
oecd.
org/
comnet/
env/
models.
nsf
OECD,
2002
Report
of
the
OECD/
UNEP
Workshop
on
the
Use
of
Multimedia
Models
for
Estimating
Overall
Environmental
Persistence
and
Long­
ENV/
JM/
MONO(
2003)
16
45
range
Transport
in
the
Context
of
PBTs/
POPs
Assessment,
ENV/
JM/
MONO(
2002)
15,
http://
www.
oecd.
org/
env/
riskassessment
OECD,
2003
Guidance
Document
on
the
Use
of
Multimedia
Models
for
Estimating
Overall
Environmental
Persistence
and
Long­
range
Transport,
http://
www.
oecd.
org/
env/
riskassessment
RIVM,
2001
van
Veen,
M.
P.,
Consexpo
3.0,
Consumer
exposure
uptake
models,
RIVM
Report
No.
612810011,
May
2001;
http://
www.
rivm.
nl/
bibliotheek/
rapporten/
612810011.
html
Trent
University
Fugacity
models
from
Mackay's
research
group
at
Trent
University
http://
www.
trentu.
ca/
cemc/
models/
models.
html
U.
S.
EPA
U.
S.
EPA/
OPPT
Exposure
Assessment
Tools
and
Models
Web
Page;
www.
epa.
gov/
oppt/
exposure
ELPOS
A.
Bayer;
Environmental
Long­
range
Transport
and
Persistence
of
Organic
Substances;
Institute
of
Environmental
System
Research;
University
of
Osnabrück
http://
www.
usf.
uos.
de/
projects/
elpos/
Chemrange
Martin
Scheringer,
ETH
Zürich,
scheringer@
tech.
chem.
ethz.
ch
http://
www.
tech.
chem.
ethz.
ch/
hungerb/
research/
product/
chemrange.
html
RIVM,
1991
Jaaps
Struis,
Simple
Treat,
RIVM
Report
No.
670208002
http://
www.
rivm.
nl/
bibliotheek/
rapporten/
670208002.
html
RIVM,
1996
Brandes
LJ,
den
Hollander
H,
van
de
Meent
D.,
Simple
Box,
RIVM
Report
No.
719101029;
http://
www.
rivm.
nl/
bibliotheek/
rapporten/
719101029.
html
OPS­
Model
EU
­
Technical
Guidance
Document
Support
of
Commission
Directive
93/
67/
EEC,
Commission
Regulation
1488/
94/
EEC
and
Directive
98/
8/
EC,
2003
Van
Jaarsveld,
J.
A.
(
1990).
An
operational
atmospheric
transport
model
for
Priority
Substances;
specifications
and
instructions
for
use.
RIVM
report
no.
222501002.
Indirect
Exposure
EU
­
Technical
Guidance
Document
Support
of
Commission
Directive
93/
67/
EEC,
Commission
Regulation
1488/
94/
EEC
and
Directive
98/
8/
EC,
2003,
Part
I,
Chapter
2
http://
ecb.
jrc.
it/
cgi­
bin/
reframer.
pl?
A=
ECB&
B=/
tgdoc/
ENV/
JM/
MONO(
2003)
16
46
ANNEX
4:
LISTING
OF
INDUSTRIAL
CATEGORIES
AND
USE
CATEGORIES.

List
of
Industry
Categories
(
Manual
for
Investigation
of
HPV
Chemicals,
Chapter
2
Annex
1)

1.
Agricultural
industry
Agricultural
industry
deals
with
the
activities
of
growing
crops
(
vegetables,
grains,
etc.)
and
raising
cattle
(
for
dairy
products,
meat
and
wool).
It
also
comprises
all
allied
activities
such
as
pest
control
(
application
of
pesticides,
veterinary
medicines),
manuring,
etc.

2.
Chemical
industry:
basic
chemicals
There
are
two
different
ICs
for
chemical
industry,
the
industry
where
substances
are
produced
through
chemical
reactions.
The
raw
materials
for
chemical
industry
come
from
petrochemical
industry
(
IC
9
`
Mineral
oil
and
fuel
industry'),
from
plant
or
animal
materials,
or
coal.
IC
2
is
dedicated
to
basic
chemicals,
which
are
substances
used
generally
throughout
all
branches
of
chemical
industry
and
usually
in
considerable
amounts.
Important
basic
chemicals
are
solvents
(
UC
48)
and
pH­
regulating
agents
(
UC
40)
(
acids,
alkalis).

3.
Chemical
industry:
chemicals
used
in
synthesis
Chemicals
used
in
synthesis
are
substances
either
regulating
the
chemical
reaction
process
(
e.
g.
catalysts)
or
being
used
as
an
intermediate
(
i.
e.
chemicals
that
are
formed
and
can
be
isolated
at
an
intermediate
step
between
starting
material
and
the
final
product
in
a
sequence
of
chemical
processes).

4.
Electrical/
electronic
industry
In
electrical/
electronic
industry
production
of
a
wide
range
of
products
is
manufactured.
It
comprises
both
the
manufacture
of
components
like
resistors,
transistors,
capacitors,
diodes,
lamps,
etc.
and
the
production
of
televisions,
radios,
computers
(
PC's
as
well
as
mainframes),
radar
installations,
complete
telephone
exchanges,
etc.
In
the
manufacturing
processes
constituent
processes
may
take
place.
The
main
constituent
processes
are
electroplating,
polymer
processing,
and
paint
application.

5.
Personal/
domestic
In
this
IC
the
use
and
application
of
substances
in
household
for
maintenance
and
care
of
houses,
furniture,
kitchenware,
gardens,
etc.,
and
personal
care
(
hygiene,
make­
up,
etc.)
is
covered.
Chemicals
used
in
this
IC
in
many
cases
will
be
present
in
formulations,
e.
g.
in
cleaners
(
soaps,
detergents,
washing
powders,
etc.),
cosmetics,
and
products
for
the
care
of
leather,
textile
and
cars.
ENV/
JM/
MONO(
2003)
16
47
6.
Public
domain
This
IC
covers
application
and
use
of
substances
in
a
variety
of
places
by
skilled
workers,
such
as
offices,
public
buildings,
waiting
rooms,
various
workshops
like
garages,
professional
cleaning
and
maintenance
of
buildings,
streets,
parks,
etc.
Also
in
this
IC
most
chemicals
will
be
present
in
formulations,
e.
g.
in
"
cleaners"
(
UC
=
9
`
Cleaning
and
washing
agents
and
disinfectants'),
nonagricultural
biocides
(
UC
=
39
`
Biocides,
non­
agricultural'),
and
products
for
the
maintenance
of
roads,
buildings,
etc.

7.
Leather
processing
industry
Leather
processing
industry
is
considered
as
the
industries
where
leather
is
made
out
of
raw
hides,
leather
is
dyed
and
where
products
are
made
out
of
leather
(
e.
g.
shoe
manufacture).

8.
Metal
extraction,
refining
and
processing
industry
This
IC
covers
the
extraction
of
metals
from
the
ores,
the
manufacture
of
primary/
secondary
steel
and
non­
ferro
metals
(
as
well
"
pure"
metals
as
alloys),
and
the
manifold
of
metal
working
processes
("
shaping")
like
cutting,
drilling,
rolling,
etc.

9.
Mineral
oil
and
fuel
industry
Mineral
oil
and
fuel
industry
involves
the
so­
called
petrochemical
industry,
which
processes
crude
mineral
oil.
By
means
of
physical
and
chemical
processes
(
e.
g.
separation
by
means
of
distillation,
cracking
and
platforming)
they
produce
a
wide
range
of
hydrocarbons
serving
as
raw
materials
for
chemical
industry
and
(
often
after
adding
a
series
of
additives)
fuels
for
heating
and
combustion
engines.

10.
Photographic
industry
Photographic
industry
is
the
industry
where
photographic
materials
are
manufactured
("
solid"
materials
like
films
and
photographic
"
papers",
but
also
preparations
­
either
in
a
solid
or
a
liquid
form
­
for
film
and
paper
processing
baths.
Also
the
processing
of
films
and
photographic
paper
is
accounted
to
photographic
industry,
including
professional
processing
in
so­
called
printshops.

11.
Polymers
industry
Polymers
industry
comprises
the
branch
of
chemical
industry
where
`
plastics'
(
thermoplastics)
are
chemically
produced
and
industries
where
processing
of
thermoplastics
and
prepolymers
takes
place
by
means
of
a
wide
range
of
techniques.

12.
Pulp,
paper
and
board
industry
Production
of
pulp,
paper
and
cardboard
out
of
wood
or
waste
paper
belongs
to
this
IC,
but
also
chemicals
used
in
reprographic
industry.

13.
Textile
processing
industry
This
IC
covers
treatment
of
fibres
("
cleaning",
spinning,
dyeing,
etc.),
weaving,
and
finishing
(
e.
g.
impregnation,
coating,
etc.).
ENV/
JM/
MONO(
2003)
16
48
14.
Paints,
lacquers
and
varnishes
industry
Apart
from
the
manufacture
of
coating
products
(
stage
of
formulation)
like
paints
this
IC
also
covers
application
of
these
products.

16.
Engineering
industry:
civil
and
mechanical
To
this
IC
industrial
activities
belong
such
as
wood
processing
industries
(
e.
g.
wooden
furniture),
motor
car
manufacture,
building
industry,
etc.

0.
Others
All
processes
and
activities,
which
can
not
be
placed
in
one
of
the
previous
ICs,
belong
to
this
IC.
An
example
is
food
processing
industry.
ENV/
JM/
MONO(
2003)
16
49
List
of
Use
Categories
(
Manual
for
Investigation
of
HPV
Chemicals,
Chapter
2
Annex
1)

The
Use
Categories
(
UC)
described
below
(
left
column),
as
they
are
proposed
by
IUCLID
can
be
used
for
that
purpose.
The
corresponding
functions
as
proposed
by
ChemUSES
(
US­
EPA,
1980)
are
listed
in
the
right
column.
A
list
of
synonyms
for
functions
according
to
ChemUSES
vs.
IUCLID
Use
category
No
is
also
presented
below.

No.
USE
CATEGORY
(
IUCLID)
No.
Function
(
ChemUSES)

1
Absorbents
and
adsorbents
131
Absorbents
60
Adsorbents
213
Dehumidifiers
2
Adhesive,
binding
agents
302
Adhesives
143
Binders
92
Spreaders
165
Stickers
280
Tackifiers
3
Aerosol
propellants
178
Aerosol
propellants
4
Anti­
condensation
agents
5
Anti­
freezing
agents
77
Antifreezes
74
De­
icers
52
Deodorants
313
Functional
fluids
6
Anti­
set­
off
and
anti­
adhesive
agents
104
Abherents
63
Antiblocking
agents
188
Anticaking
agents
300
Detackifiers
233
Dusting
agents
144
Parting
agents
7
Soil
retardants
7
Anti­
static
agents
328
Antistatic
agents
89
Electroconductive
coating
agents
318
Humectants
8
Bleaching
agents
304
Bleaching
assistants
132
Bleaching
agents
9
Cleaning/
washing
agents
and
additives
293
Antiredeposition
agents
180
Boil­
off
assistants
242
Cleaners
173
Detergents
78
Pre­
spotting
agents
274
Scouring
agents
261
Shrinkage
controllers
14
Soaping­
off
assistants
294
Soil
release
agents
10
Colouring
agents
5
Bloom
agents
86
Colouring
agents
174
Coupling
agents
(
dyes)
267
Dyes
ENV/
JM/
MONO(
2003)
16
50
20
Fluorescent
agents
248
Lakes
381
Luminescent
agents
235
Mercerising
assistants
128
Opacifiers
139
Pearlizing
agents
125
Pigments
83
Stains
11
Complexing
agents
177
Antiprecipitants
124
Complexing
agents
10
Sequestering
agents
12
Conductive
agents
161
Electrical
conductive
agents
383
Electrode
materials
245
Electrolytes
313
Functional
fluids
13
Construction
materials
and
additives
324
Case­
hardening
agents
355
Concrete
additives
361
Embrittlement
inhibitors
375
Materials
for
shaping
250
Reinforcing
agents
349
Water­
reducing
agents
14
Corrosion
inhibitors
230
Antioxidants
64
Antiscaling
agents
323
Corrosion
inhibitors
15
Cosmetics
301
Antiperspirants
167
Cosmetic
ingredients
16
Dust
binding
agents
26
Dust
control
agents
17
Electroplating
agents
353
Brighteners
32
Fume
suppressants
18
Explosives
179
Detonators
363
Explosion
inhibitors
158
Explosives
27
Incendiaries
19
Fertilisers
34
Fertilisers
20
Fillers
351
Fillers
(
augmentation)
212
Fillers
(
patching)
371
Surface
coating
additives
127
Swelling
agents
58
Weighting
agents
(
textile
technology)

21
Fixing
agents
291
Anticrock
agents
347
Antistripping
agents
268
Barrier
coating
agents
295
Fixatives
134
Fixing
agents
(
fragrances)
112
Fixing
agents
(
textile
technology)
227
Mordents
22
Flame
retardants
and
fire
preventing
25
Fire
extinguishing
agents
agents
332
Flame
retardants
ENV/
JM/
MONO(
2003)
16
51
23
Flotation
agents
163
Activators
(
ore
processing)
190
Flocculating
agents
297
Flotation
agents
360
Modifiers
24
Flux
agents
for
casting
25
Foaming
agents
358
Blowing
agents
133
Chemical
blowing
agents
94
Frothers
50
Physical
blowing
agents
26
Food/
feedstuff
additives
214
Acidulants
66
Feed
additives
145
Food
additives
80
Sweeteners
(
taste)

27
Fuels
247
Fuels
28
Fuel
additives
329
Antifouling
agents
76
Antiknock
agents
183
Deposit
modifiers
306
Fuel
additives
138
Sweeteners
(
petroleum
technology)

29
Heat
transferring
agents
72
Coolants
313
Functional
fluids
199
Heat
transfer
agents
216
Quenchers
208
Refrigerants
30
Hydraulic
fluids
and
additives
313
Functional
fluids
65
Hydraulic
fluids
256
Transmission
fluids
31
Impregnation
agents
102
Delustrants
98
Sizes
258
Water
repellents
23
Waterproofing
agents
32
Insulating
materials
254
Acoustical
insulating
material
311
Electrical
insulating
material
314
Heat
insulating
materials
162
Insulating
materials
33
Intermediates
146
Inorganic
intermediates
115
Monomers
290
Organic
intermediates
43
Prepolymers
34
Laboratory
chemicals
238
Analytical
and
product
testing
122
Chelating
agents
107
Deionisers
373
Extraction
agents
69
Indicators
325
Oxidation­
reduction
indicators
374
Reagents
35
Lubricants
and
additives
119
Antiseize
agents
313
Functional
fluids
ENV/
JM/
MONO(
2003)
16
52
148
Internal
lubricating
agents
195
Lubricant
additives
364
Lubricating
agents
346
Oiliness
agents
249
Penetrants
312
Slip
agents
36
Odour
agents
79
Flavours
and
fragrances
339
Odorants
37
Oxidising
agents
149
Oxidisers
38
Plant
protection
products,
agricultural
166
Animal
repellents
333
Bactericides
108
Biocides
97
Decontaminats
270
Fumigants
362
Fungicides
275
Herbicides
155
Insect
attractants
348
Insect
repellents
330
Insecticides
252
Nematocides
253
Pesticides
264
Rodenticides
39
Biocides,
non­
agricultural
287
Algicides
1
Antifouling
agents
140
Disinfectants
118
Preservatives
116
Slime
preventatives
40
pH­
regulating
agents
172
Laundry
sours
266
pH
control
agents
191
pH
indicators
41
Pharmaceuticals
42
Photochemicals
122
Chelating
agents
198
Desensitisers
(
explosives)
299
Desensitisers
(
photography)
182
Developers
286
Intensifiers
(
photography)
285
Light
stabilisers
344
Photosensitive
agents
303
Sensitisers
43
Process
regulators
321
Accelerators
46
Activators
(
chemical
processes)
239
Activators
(
enzymes)
110
Adhesion
promoters
4
Antifelting
agents
352
Antislip
finishing
agents
206
Antistaining
agents
194
Antiwebbing
agents
281
Builders
222
Carbonising
agents
164
Carriers
19
Catalyst
supports
ENV/
JM/
MONO(
2003)
16
53
170
Catalysts
31
Chain
extenders
113
Chain
terminators
141
Chain
transfer
agents
122
Chelating
agents
114
Coagulants
278
Coalescents
357
Coalescing
agents
315
Crabbing
assistants
228
Crosslinking
agents
226
Curing
agents
(
concrete)
369
Curing
agents
(
polymer
technology)
18
Currying
agents
236
Deasphalting
agents
342
Defoamers
365
Degumming
agents
137
Dehairing
agents
73
Dehydrating
agents
366
De­
inkers
84
Delignification
agents
30
Depolymerisation
agents
367
Depressants
292
Desising
agents
259
Dispersants
317
Dryers
150
Dye
carriers
255
Dye
levelling
agents
307
Dye
retardants
211
Dye
retention
aids
341
Enzyme
inhibitors
157
Enzymes
284
Finishing
agents
337
Formation
aids
331
Fuel
oxidisers
117
Fulling
agents
103
Initiators
359
Intensifiers
(
printing)
171
Kier
boiling
assistants
24
Nucleating
agents
96
Peptising
agents
75
Pitch
control
agents
121
Polymerisation
additives
209
Polymerisation
inhibitors
21
Prevulcanisation
inhibitors
153
Refining
agents
223
Repulping
aids
136
Retarders
296
Retention
aids
338
Rubber
compounding
agents
51
Scavengers
326
Solubilising
agents
310
Weighting
agents
(
petroleum
technology)

44
Reducing
agents
244
Reducers
45
Reprographic
agents
225
Toners
46
Semiconductors
202
Semiconductors
378
Photovoltaic
agents
ENV/
JM/
MONO(
2003)
16
54
47
Softeners
269
Bates
231
Devulcanising
agents
28
Elasticisers
265
Emollients
185
Plasticisers
29
Softeners
147
Water
softeners
48
Solvents
229
Degreasers
82
Dewaxing
solvents
373
Extraction
agents
320
Paint
and
varnish
removers
16
Reaction
media
271
Solvents
49
Stabilisers
277
Anticracking
agents
12
Antifume
agents
129
Antihydrolysis
agents
168
Antiozonants
230
Antioxidants
120
Antilivering
agents
282
Antiplasticisers
160
Antisagging
agents
68
Antisettling
agents
88
Bloom
inhibitors
123
Coupling
agents
(
polymers)
159
Emulsifiers
87
Heat
stabilisers
54
Stabilisers
36
Ultraviolet
absorbers
50
Surface­
active
agents
41
Antifloating
agents
234
Antifogging
agents
109
Surfactants
243
Wetting
agents
51
Tanning
agents
316
Tanning
agents
52
Viscosity
adjustors
152
Antiflooding
agents
120
Antilivering
agents
343
Antiskinning
agents
221
Gelling
agents
262
Pour
point
depressants
272
Thickeners
334
Thixotropic
agents
240
Turbulence
suppressors
135
Viscosity
adjustors
15
Viscosity
index
improvers
53
Vulcanising
agents
288
Vulcanising
agents
54
Welding
and
soldering
agents
101
Brazing
agents
22
Fluxing
agents
0
Other
204
Ablatives
105
Abrasives
196
Activators
(
luminescence)
354
Aerating
agents
ENV/
JM/
MONO(
2003)
16
55
47
Air
entraining
agents
376
Alloying
agents
90
Anticratering
agents
48
Anticreasing
agents
99
Antifogging
agents
218
Antipilling
agents
350
Antiskid
agents
6
Blasting
abrasives
70
Bluing
agents
220
Bright
dips
93
Chemical
raw
materials
298
Clarifiers
260
Cloud
point
depressants
130
Coating
agents
283
Collectors
335
Coupling
agents
(
solutions)
215
Culture
nutrients
81
Deaerating
agents
309
Deblooming
agents
85
Dechlorinating
agents
73
Dehydrating
agents
107
Deionisers
232
Demulsifiers
200
Denaturants
49
Descaling
agents
205
Dewatering
aids
356
Discharge
printing
agents
38
Drainage
aids
44
Drilling
mud
additives
322
Dry
strength
additives
39
Dye
stripping
agents
100
Electron
emission
agents
340
Eluting
agents
372
Embalming
agents
186
Encapsulating
agents
57
Enhanced
oil
recovery
agents
308
Entraining
agents
319
Etching
agents
336
Evaporation
control
agents
373
Extraction
agents
207
Fiber­
forming
compounds
368
Filtration
aids
56
Flatting
agents
79
Flavours
and
fragrances
142
Fluid
loss
additives
313
Functional
fluids
193
Greaseproofing
agents
184
"
Grinding,
lapping,
sanding
and"
192
Hormones
246
Humidity
indicators
210
Hydrotropic
agents
181
Impact
modifiers
380
Incandescent
agents
69
Indicators
2
Ion
exchange
agents
91
Lachrymators
33
Latex
compounding
agents
53
Leaching
agents
156
Leather
processing
agents
ENV/
JM/
MONO(
2003)
16
56
370
Liquid
crystals
381
Luminescent
agents
379
Magnetic
agents
67
Mar
proofing
agents
289
Metal
conditioners
95
Metal
strippers
37
Metal
treating
agents
327
Milling
aids
237
Obscuring
agents
197
Oil
repellents
62
Optical
quenchers
382
Osmotic
membranes
17
Papermaking
agents
55
Phosphatising
agents
203
Phosphorescent
agents
59
Pickling
agents
217
Pickling
inhibitors
251
Plant
growth
regulators
176
Plastics
additives
224
Plastics
for
shaping
169
Plating
agents
8
Poison
gas
decontaminants
3
Polymer
strippers
111
Pore
forming
agents
151
Precipitating
agents
106
Protective
agents
45
Radioactivity
decontaminants
374
Reagents
219
Refractive
index
modifiers
241
Refractories
154
Resists
9
Rinse
aids
71
Ripening
agents
187
Rubber
for
shaping
201
Rubber
reclaiming
agents
189
Rubbing
fastness
agents
276
Rust
inhibitors
11
Rust
removers
263
Scrooping
agents
42
Sealants
98
Sizes
126
Slime
control
agents
305
Soil
conditioners
61
Strippers
40
Tar
removers
345
Tarnish
inhibitors
13
Tarnish
removers
279
Textile
specialities
257
Vat
printing
assistants
273
Wax
strippers
35
Well
treating
agents
175
Wet
strength
additives
377
X­
ray
absorbents
ENV/
JM/
MONO(
2003)
16
57
List
of
synonyms
for
functions
according
to
ChemUSES
(
US­
EPA,
1980)
vs.
IUCLID
Use
category
No.

No.
ChemUSES
Function
Use
category
IUCLID
(
No.)

104
Abherents
6
204
Ablatives
55
105
Abrasives
0
131
Absorbents
1
321
Accelerators
43
214
Acidulants
26
254
Acoustical
insulating
material
32
46
Activators
(
chemical
processes)
43
163
Activators
(
ore
processing)
23
196
Activators
(
luminescence)
55
239
Activators
(
enzymes)
43
110
Adhesion
promoters
43
302
Adhesives
2
60
Adsorbents
1
354
Aerating
agents
0
178
Aerosol
propellents
3
47
Air
entraining
agents
0
287
Algicides
39
376
Alloying
agents
0
238
Analytical
and
product
testing
34
166
Animal
repellents
38
63
Antiblocking
agents
6
188
Anticaking
agents
6
277
Anticracking
agents
49
90
Anticratering
agents
0
48
Anticreasing
agents
0
291
Anticrock
agents
21
4
Antifelting
agents
43
41
Antifloating
agents
50
152
Antiflooding
agents
52
234
Antifogging
agents
50
99
Antifogging
agents
0
1
Antifouling
agents
39
329
Antifouling
agents
28
77
Antifreezes
5
12
Antifume
agents
49
129
Antihydrolysis
agents
49
76
Antiknock
agents
28
120
Antilivering
agents
49,
52
230
Antioxidants
14,
49
168
Antiozonants
49
301
Antiperspirants
15
218
Antipilling
agents
55
282
Antiplasticisers
49
177
Antiprecipitants
11
293
Antiredeposition
agents
9
160
Antisagging
agents
49
64
Antiscaling
agents
14
119
Antiseize
agents
35
68
Antisettling
agents
49
350
Antiskid
agents
0
343
Antiskinning
agents
52
352
Antislip
finishing
agents
43
206
Antistaining
agents
43
328
Antistatic
agents
7
347
Antistripping
agents
21
194
Antiwebbing
agents
43
333
Bactericides
38
268
Barrier
coating
agents
21
269
Bates
47
143
Binders
2
No.
ChemUSES
Function
Use
category
IUCLID
(
No.)

108
Biocides
38
6
Blasting
abrasives
0
132
Bleaching
agents
8
304
Bleaching
assistants
8
5
Bloom
agents
10
88
Bloom
inhibitors
49
358
Blowing
agents
25
70
Bluing
agents
0
180
Boil­
off
assistants
9
101
Brazing
agents
54
220
Bright
dips
0
353
Brighteners
17
281
Builders
43
222
Carbonising
agents
43
164
Carriers
43
324
Case­
hardening
agents
13
170
Catalysts
43
19
Catalyst
supports
43
31
Chain
extenders
43
113
Chain
terminators
43
141
Chain
transfer
agents
43
122
Chelating
agents
34,
42,
43
133
Chemical
blowing
agents
25
93
Chemical
raw
materials
0
298
Clarifiers
0
242
Cleaners
9
260
Cloud
point
depressants
0
114
Coagulants
43
278
Coalescents
43
357
Coalescing
agents
43
130
Coating
agents
0
283
Collectors
0
86
Colouring
agents
10
124
Complexing
agents
11
355
Concrete
additives
13
72
Coolants
29
323
Corrosion
inhibitors
14
167
Cosmetic
ingredients
15
123
Coupling
agents
(
polymers)
49
174
Coupling
agents
(
dyes)
10
335
Coupling
agents
(
solutions)
55
315
Crabbing
assistants
43
228
Crosslinking
agents
43
215
Culture
nutrients
0
226
Curing
agents
(
concrete)
43
369
Curing
agents
(
polymer
technology)
43
18
Currying
agents
43
366
De­
inkers
43
81
Deaerating
agents
0
236
Deasphalting
agents
43
309
Deblooming
agents
0
85
Dechlorinating
agents
55
97
Decontaminats
38
342
Defoamers
43
229
Degreasers
48
365
Degumming
agents
43
137
Dehairing
agents
43
213
Dehumidifiers
1
73
Dehydrating
agents
0,
34
74
Deicers
5
107
Deionizers
0,
34
ENV/
JM/
MONO(
2003)
16
58
84
Delignification
agents
43
102
Delustrants
31
232
Demulsifiers
0
200
Denaturants
0
52
Deodorants
5
30
Depolymerisation
agents
43
183
Deposit
modifiers
28
367
Depressants
43
49
Descaling
agents
0
198
Desensitisers
(
explosives)
42
299
Desensitisers
(
photography)
42
292
Desizing
agents
43
300
Detackifiers
6
173
Detergents
9
179
Detonators
18
182
Developers
42
231
Devulcanising
agents
47
205
Dewatering
aids
0
82
Dewaxing
solvents
48
356
Discharge
printing
agents
0
140
Disinfectants
39
259
Dispersants
43
38
Drainage
aids
0
317
Dryers
43
44
Drilling
mud
additives
0
322
Dry
strength
additives
0
26
Dust
control
agents
16
233
Dusting
agents
6
150
Dye
carriers
43
255
Dye
leveling
agents
43
307
Dye
retardants
43
211
Dye
retention
aids
43
39
Dye
stripping
agents
0
267
Dyes
10
28
Elasticisers
47
161
Electrical
conductive
agents
12
311
Electrical
insulating
material
32
89
Electroconductive
coating
agents
7
383
Electrode
materials
12
245
Electrolytes
12
100
Electron
emission
agents
0
340
Eluting
agents
0
372
Embalming
agents
0
361
Embrittlement
inhibitors
13
265
Emollients
47
159
Emulsifiers
49
186
Encapsulating
agents
0
57
Enhanced
oil
recovery
agents
0
308
Entraining
agents
0
341
Enzyme
inhibitors
43
157
Enzymes
43
319
Etching
agents
0
336
Evaporation
control
agents
0
363
Explosion
inhibitors
18
158
Explosives
18
373
Extraction
agents
34,
48
66
Feed
additives
26
34
Fertilisers
19
207
Fiber­
forming
compounds
0
212
Fillers
(
patching)
20
351
Fillers
(
augmentation)
20
368
Filtration
aids
0
284
Finishing
agents
43
25
Fire
extinguishing
agents
22
295
Fixatives
21
112
Fixing
agents
(
textile
technology)
21
134
Fixing
agents
(
fragrances)
21
332
Flame
retardants
22
56
Flatting
agents
0
79
Flavours
and
fragrances
0,
36
190
Flocculating
agents
23
297
Flotation
agents
23
142
Fluid
loss
additives
0
20
Fluorescent
agents
10
22
Fluxing
agents
54
145
Food
additives
26
337
Formation
aids
43
94
Frothers
25
306
Fuel
additives
28
331
Fuel
oxidisers
43
247
Fuels
27
117
Fulling
agents
43
32
Fume
suppressants
17
270
Fumigants
38
313
Functional
fluids
0,
5,
12,
29,
30,
35
362
Fungicides
38
221
Gelling
agents
52
193
Greaseproofing
agents
0
184
Grinding,
lapping,
sanding
and
polishing
abrasives
0
199
Heat
transfer
agents
29
314
Heat
insulating
materials
32
87
Heat
stabilisers
49
275
Herbicides
38
192
Hormones
0
318
Humectants
7
246
Humidity
indicators
0
65
Hydraulic
fluids
30
210
Hydrotropic
agents
0
181
Impact
modifiers
0
380
Incandescent
agents
0
27
Incendiaries
18
69
Indicators
0,
34
103
Initiators
43
146
Inorganic
intermediates
33
155
Insect
attractants
38
348
Insect
repellents
38
330
Insecticides
38
162
Insulating
materials
32
286
Intensifiers
(
photography)
42
359
Intensifiers
(
printing)
43
148
Internal
lubricating
agents
35
2
Ion
exchange
agents
0
171
Kier
boiling
assistants
43
91
Lachrymators
0
248
Lakes
10
33
Latex
compounding
agents
0
172
Laundry
sours
40
53
Leaching
agents
0
156
Leather
processing
agents
0
285
Light
stabilisers
42
370
Liquid
crystals
0
195
Lubricant
additives
35
364
Lubricating
agents
35
381
Luminescent
agents
0,
10
379
Magnetic
agents
0
67
Mar
proofing
agents
55
375
Materials
for
shaping
13
235
Mercerising
assistants
10
289
Metal
conditioners
0
37
Metal
treating
agents
0
95
Metal
strippers
0
327
Milling
aids
0
360
Modifiers
23
ENV/
JM/
MONO(
2003)
16
59
115
Monomers
33
227
Mordents
21
252
Nematocides
38
24
Nucleating
agents
43
237
Obscuring
agents
0
339
Odorants
36
197
Oil
repellents
0
346
Oiliness
agents
35
128
Opacifiers
10
62
Optical
quenchers
0
290
Organic
intermediates
33
382
Osmotic
membranes
0
325
Oxidation­
reduction
indicators
34
149
Oxidisers
37
320
Paint
and
varnish
removers
48
17
Papermaking
agents
0
144
Parting
agents
6
139
Pearlising
agents
10
249
Penetrants
35
96
Peptising
agents
43
253
Pesticides
38
191
pH
indicators
40
266
pH
control
agents
40
55
Phosphatising
agents
0
203
Phosphorescent
agents
0
344
Photosensitive
agents
42
378
Photovoltaic
agents
42
50
Physical
blowing
agents
25
217
Pickling
inhibitors
0
59
Pickling
agents
0
125
Pigments
10
75
Pitch
control
agents
43
251
Plant
growth
regulators
0
185
Plasticisers
47
176
Plastics
additives
0
224
Plastics
for
shaping
0
169
Plating
agents
0
8
Poison
gas
decontaminants
0
3
Polymer
strippers
0
121
Polymerisation
additives
43
209
Polymerisation
inhibitors
43
111
Pore
forming
agents
0
262
Pour
point
depressants
52
78
Pre­
spotting
agents
9
151
Precipitating
agents
0
43
Prepolymers
33
118
Preservatives
39
21
Prevulcanisation
inhibitors
43
106
Protective
agents
0
216
Quenchers
29
45
Radioactivity
decontaminants
0
16
Reaction
media
48
374
Reagents
0,
34
244
Reducers
44
153
Refining
agents
43
219
Refractive
index
modifiers
0
241
Refractories
0
208
Refrigerants
29
250
Reinforcing
agents
13
223
Repulping
aids
43
154
Resists
0
136
Retarders
43
296
Retention
aids
43
9
Rinse
aids
0
71
Ripening
agents
0
264
Rodenticides
38
338
Rubber
compounding
agents
43
187
Rubber
for
shaping
0
201
Rubber
reclaiming
agents
0
189
Rubbing
fastness
agents
0
11
Rust
removers
0
276
Rust
inhibitors
0
51
Scavengers
43
274
Scouring
agents
9
263
Scrooping
agents
0
42
Sealants
0
202
Semiconductors
46
303
Sensitisers
42
10
Sequestering
agents
11
261
Shrinkage
controllers
9
98
Sizes
0,
31
126
Slime
control
agents
0
116
Slime
preventatives
39
312
Slip
agents
35
14
Soaping­
off
assistants
9
29
Softeners
47
305
Soil
conditioners
0
294
Soil
release
agents
9
7
Soil
retardants
6
326
Solubilising
agents
43
271
Solvents
48
92
Spreaders
2
54
Stabilisers
49
83
Stains
10
165
Stickers
2
61
Strippers
0
371
Surface
coating
additives
20
109
Surfactants
50
138
Sweeteners
(
petroleum
technology)
28
80
Sweeteners
(
taste)
26
127
Swelling
agents
20
280
Tackifiers
2
316
Tanning
agents
51
40
Tar
removers
0
13
Tarnish
removers
0
345
Tarnish
inhibitors
0
279
Textile
specialities
0
272
Thickeners
52
334
Thixotropic
agents
52
225
Toners
45
256
Transmission
fluids
30
240
Turbulence
suppressors
52
36
Ultraviolet
absorbers
49
257
Vat
printing
assistants
0
135
Viscosity
adjustors
52
15
Viscosity
index
improvers
52
288
Vulcanising
agents
53
147
Water
softeners
47
258
Water
repellents
31
349
Water­
reducing
agents
13
23
Waterproofing
agents
31
273
Wax
strippers
0
310
Weighting
agents
(
petroleum
technology)
43
58
Weighting
agents
(
textile
technology)
20
35
Well
treating
agents
0
175
Wet
strength
additives
0
243
Wetting
agents
50
377
X­
ray
absorbents
0
ENV/
JM/
MONO(
2003)
16
60
Category
of
Product/
general
characterisation
Subcategories
(
EU
Technical
Guidance
Document
Chapter
2
Appendix
II)

1.
CLEANER
/
POLISH
The
category
covers
all
products
that
are
used
in
the
household
for
cleaning,
polishing
and
care.
Some
subcategories
can
be
defined
by
different
use
characteristics.
A
comprehensive
overview
on
household
cleaners
and
its
subcategories
has
been
published
by
the
IKW
(
IKW,
2001)
 
Cleaning
of
machines
and
vehicles
(
e.
g.
cars,
bikes,
motorbikes)
 
General
household
(
All
Purpose
Cleaners)
 
Dish
washing,
manual
 
Dish
washing,
machine
 
Sanitary
cleaners
 
Textile
cleaners
e.
g.
Powder
Laundry
Detergents,
Laundry
Liquid
Detergents
 
Oven
cleaners
 
Shoe
and
leather
cleaner
 
Furniture
cleaners
 
Drain
cleaners
 
Metal
cleaners
2.
ADHESIVE
/
SEALANT
The
category
covers
all
products
that
are
used
in
the
household
as
adhesives
or
sealants.
Some
subcategories
can
be
defined
by
different
use
characteristics
(
The
list
of
subcategories
of
adhesives
has
been
prepared
by
the
WHO/
IPCS).
 
General
purpose
adhesive
 
Floor
covering
adhesives
 
Dental
plate
cement
 
Fabric
adhesive
 
Film
cement,
photographic
 
Leather
adhesive
 
Metal
adhesive
 
Paper
adhesive
 
Plastic
adhesive
 
Rubber
adhesive
 
Wallboard
joint
cement
 
Wallpaper
adhesive
 
Wood
adhesive
3.
PRINTING
/
WRITING
MATERIAL
The
category
covers
all
products
that
are
used
in
the
household
for
writing
and
printing.
Some
subcategories
can
be
defined
by
different
use
characteristics:
(
The
list
of
subcategories
of
adhesives
has
been
prepared
by
the
WHO/
IPCS).
 
°
Dye
 
°
Ink
 
°
Etching
fluid
 
°
Correction
fluid
 
°
Crayon
 
°
Pen
marker
 
°
Toner
PAINTING
MATERIAL
AND
ADDITIVES
The
category
covers
all
products
that
are
painted
to
an
area
for
renewing,
or
to
protect
the
areas
against
wetness
or
corrosion
etc.
Some
subcategories
can
be
defined
by
different
use
characteristics.
The
classification
of
subcategories
has
been
prepared
according
to
Baumann
&
Muth
(
1997)
and
Bremmer
and
van
Veen
(
2000a).
 
Solvent
based
paint
 
Water
based
paint
 
Resin
based
paints
 
Aerosol
paints
 
Paints
for
special
purposes
 
Industrial
paints
 
Varnish
 
Bleaching
paints
 
Paints
for
conservation
 
Thinner
 
Paint
remover
4.
FUELS
This
category
covers
products
that
are
used
for
feed
machines
(
cars,
motorbikes)
or
lamps
or
to
lighten
fires.
 
Gasoline
 
Fuel
oil
 
Liquid
lamp
oils
and
grill
lighters
ENV/
JM/
MONO(
2003)
16
61
 
Solid
grill
lighters
 
Solid
lighteners,
other
5.
BLEACH
/
DISINFECTANT
/
STERILIZER
The
category
covers
all
products
that
are
used
in
the
household
as
a
bleach
or
for
sterilisation.
Some
subcategories
can
be
defined
by
different
use
characteristics.
 
Bleaches
 
Sterilisers
6.
REMOVERS
The
category
covers
all
products
that
are
used
in
the
household
to
remove
substances,
from
surfaces
and
thus
cleaning
them.
Some
subcategories
can
be
defined
by
different
use
characteristics:
 
Adhesive/
glue
remover
 
Dye/
ink
remover
 
Seal
remover
 
Polish
remover
 
Limescale
remover/
descaler
 
Oil/
grease
remover
 
Rust
remover
 
Stain
remover
 
Wall
paper
remover
7.
PHOTOGRAPHIC
CHEMICAL
The
category
covers
all
products
in
the
household
that
are
referred
to
photography.
Some
subcategories
can
be
defined
by
different
use
characteristics:
 
Photographic
chemicals
 
Photographic
paper
8.
TEXTILE
CHEMICAL
The
category
covers
all
products
that
are
exposure
related
to
the
use
of
textiles.
Some
subcategories
can
be
defined
by
different
use
characteristics.
 
Textile
colours/
dyes
 
Emission
from
textiles
 
Residues
from
cleaning
textiles
 
Fabric
softeners
 
Fire
protecting
agents
in
textiles
9.
VEHICLE
MAINTENANCE
The
category
covers
all
products
that
are
used
in
the
household
to
make
vehicles
(
cars,
bikes,
motorbikes,
caravans,
boats
etc.)
ready
for
use.
Cleaning
is
covered
by
the
category
"
cleaner/
polish".
Some
subcategories
can
be
defined
by
different
use
characteristics:
 
°
Lubricants
 
°
Repairing
material
 
°
Antifreeze
(
vehicle)
 
°
Screen
wash
 
°
Brake
fluid
 
°
Fuel
additive
 
°
Radiator
fluid
 
°
Transmission
fluid
10.
COSMETIC
/
PERSONAL
HYGIENE
PRODUCT
The
category
covers
all
products
that
are
used
in
the
household
to
clean
and
care
the
body
in
particular
e.
g.
hair
and
skin.
Some
subcategories
can
be
defined
by
different
use
characteristics.
Categories
of
cosmetics
are
extensively
described
by
the
compilation
of
cosmetic
frame
formulations
(
COLIPA,
2000).
 
°
Rinse
off
products
(
e.
g.
Hand
Dishwashing
Liquids)
 
°
Non­
rinse
products
 
°
Spraying
 
°
Products
that
can
contact
mucous
membranes
11.
CONTAMINATION
OF
FOOD
The
category
covers
exposures
that
can
be
referred
to
the
consumption
of
food.
In
particular,
it
is
referred
to
contaminations
of
food
and
is
subcate­
gorised
to
the
different
kinds
of
food.
Most
of
the
data
referring
to
this
type
of
exposure
are
available
from
food
surveillance
studies
(
e.
g.
BGVV,
1995).
Categories
of
food
consumption
should
be
taken
according
to
the
EFG
food
grouping
system
(
EFCOSUM,
2001).
 
Contamination
of
food
by
processing
and
packaging
material
12.
AIR
CONTAMINANT
/
POLLUTANT
The
category
covers
all
exposures
that
are
referred
to
the
emission
of
chemicals
from
materials
in
the
household
except
textiles
ENV/
JM/
MONO(
2003)
16
62
 
Furniture
chemicals
 
Building
chemicals
 
Emissions
from
vehicles
(
e.
g.
cars)

13.
TOY
/
JOKE
/
CHILDREN'S
PLAYTHING
(
Bremmer
and
van
Veen,
2001)

14.
OTHER
CATEGORIES
NOT
MENTIONED
OTHERWISE
°
 
Refrigerant,
coolant
 
Solvent
 
Water
softener
 
Aerosol
propellant
 
Aquarium
product
 
Art/
craft
material
 
Deodorizer/
air
freshener
 
Sports
product
 
Swimming
pool
product
 
Waterproofing
compound
 
Agricultural
products
other
than
pesticides
 
Medical
devices
 
Piercings
ENV/
JM/
MONO(
2003)
16
63
EU
Categories
for
biocidal
Products
and
Substances
(
EU
Directive
98/
8/
EC)

Number
Product
Type
Description
Main
Group
1:
Disinfectants
&
General
Biocidal
Products
1
Human
hygiene
biological
products
Used
for
human
hygiene
purposes.
2
Private
and
public
health
area
disinfectants
and
other
biocidal
products
Used
for
the
disinfection
of
air,
surfaces,
materials,
equipment
and
furniture
which
are
not
used
for
direct
food
or
feed
contact
in
private,
public
or
industrial
areas,
including
hospitals,
as
well
as
products
used
as
algaecides.
Usage
areas
include
swimming
pools,
aquariums,
bathing
and
other
waters;
air­
conditioning
units;
walls
and
floors
in
health
and
other
institutions;
chemical
toilets,
waste
water,
hospital
waste,
soil
and
other
substrates
(
in
playgrounds).
3
Veterinary
hygiene
biocidal
products
Includes
products
used
in
areas
in
which
animals
are
housed,
kept
or
transported.
4
Food
and
feed
area
disinfectants
Used
for
the
disinfection
of
equipment,
containers,
consumption
utensils,
surfaces
or
pipework
associated
with
the
production,
transport,
storage,
or
consumption
of
food,
feed
or
drink
(
including
drink
water)
for
humans
and
animals.
5
Drinking
water
disinfectants
For
both
humans
and
animals.
Main
Group
2
Preservatives
6
In­
can
preservatives
Used
for
the
preservation
of
manufactured
products,
other
than
foodstuffs
or
feeding
stuffs,
in
containers
by
the
control
of
microbial
deterioration
to
ensure
their
shelf
life.
7
Film
preservatives
Used
for
the
preservation
of
films
or
coatings
by
the
control
of
microbial
deterioration
in
order
to
protect
the
initial
properties
of
the
surface
of
materials
or
objects
such
as
paints,
plastics,
sealants,
wall
adhesives,
binders,
papers,
art
works
etc.
8
Wood
preservatives
For
wood
from
and
including
saw­
mill
stage,
and
wood
products
(
including
preventative
and
curative
products).
9
Fibre,
leather,
rubber
and
polymerised
materials
preservatives
Includes
the
preservation
of
fibrous
materials,
such
as
paper
or
textile
products.
10
Masonry
preservatives
Used
for
the
preservation
and
remedial
treatment
of
masonry
or
other
construction
materials
other
than
wood
by
the
control
of
microbiological
algal
attack.
11
Preservatives
for
liquid­
cooling
and
processing
systems
Use
for
the
preservation
of
water
and
other
liquids
used
in
cooling
and
processing
systems
by
the
control
of
harmful
organisms
such
as
microbes,
algae
and
mussels
(
not
drinking
water
preservation
products).
12
Slimicides
Used
for
the
prevention
or
control
of
slime
growth
on
materials,
equipment
and
structures,
used
in
industrial
processes,
e.
g.
on
wood
and
ENV/
JM/
MONO(
2003)
16
64
paper
pulp,
and
porous
sand
strata
in
oil
extraction.
13
Metalworking­
fluids
preservatives
Products
used
for
the
preservation
of
metalworking
fluids
by
the
control
of
microbial
deterioration.
Main
Group
3:
Pest
Control
14
Rodenticides
Control
of
mice,
rats
or
other
rodents.
15
Avicides
control
of
birds.
16
Molluscicides
Control
of
molluscs,
e.
g.
snails
that
may
clog
pipes.
17
Piscicides
Control
of
fish;
excludes
products
for
the
treatment
of
fish
diseases.
18
Insecticides,
acaricides
and
to
control
other
arthropods
e.
g.
insects
arachnids
and
crustaceans
19
Repellents
or
attractants
Used
to
control,
harmful
organisms
(
invertebrates
such
as
fleas,
vertebrates
such
as
birds),
by
repelling
or
attracting,
including
those
that
are
used
for
human
or
veterinary
hygiene
either
directly
or
indirectly.
Main
Group
4:
Other
Biocidal
Products
20
Preservatives
for
food
and
feedstocks
Used
for
the
preservation
of
food
or
feedstuffs
by
the
control
of
harmful
organisms.
21
Antifouling
products
Used
to
control
growth
and
settlement
of
fouling
organisms
(
microbes
and
higher
forms
of
plant
and
animal
species)
on
vessels,
aquaculture
equipment
or
other
structures
used
in
water.
22
Embalming
or
taxidermist
fluids
Used
for
the
disinfection
and
preservation
of
human
or
animal
corpses,
or
parts
thereof.
23
Control
of
vertebrates
i.
e.
vermin
