Kentucky
Portion
of
the
Cincinnati­
Hamilton,
OH­
KY­
IN
CMSA
Boone
Pendleton
Campbell
Kenton
Grant
Gallatin
The
Cincinnati­
Hamilton
CMSA
was
listed
in
2001
as
being
the
24rd
largest
MSA
within
the
United
States.
This
MSA
encompasses
three
states
and
thirteen
counties.
It
includes
Dearborn
and
Ohio
Counties
in
Indiana,
Butler,
Brown,
Clermont,
Hamilton,
and
Warren
Counties
in
Ohio,
and
Boone,
Campbell,
Gallatin,
Grant,
Kenton,
and
Pendleton
Counties
in
Kentucky.

This
is
the
northern
most
geographic
region
of
Kentucky
and
the
apex
of
an
industrial
triangle
anchored
by
Louisville
on
the
southwest
and
Lexington
on
the
southeast.
Within
the
triangle
is
more
than
a
third
of
the
state's
population
and
nearly
one­
half
of
its
manufacturing
jobs.
The
interstate
highway
system
places
these
three
metropolitan
areas
within
less
than
two
hours
driving
from
each
other.
Butler
Cnty,
OH
Dearborn
Cnty,
IN
Ohio
Cnty,
IN
Warren
Cnty,
OH
Hamilton
Cnty,
OH
Clermont
Cnty,
OH
Brown
Cnty,
OH
2
BOONE
COUNTY,
KENTUCKY
Boone
County
is
part
of
the
Cincinnati­
Hamilton
Metropolitan
Statistical
Area
(
MSA)
and
is
located
to
the
west
of
Kenton
County,
Kentucky,
to
the
north
of
Grant
County,
Kentucky,
and
to
the
southwest
of
Cincinnati,
Ohio.

Geography/
Topography
Boone
County
has
a
land
area
of
246
square
miles
and
is
located
on
the
banks
of
the
Ohio
River
in
the
tri­
state
area
of
Kentucky,
Ohio
and
Indiana.

Meteorological
Information
Wind
speed/
wind
direction
information
shows
that
the
majority
of
the
time
for
the
period
1988
 
1992,
the
wind
in
the
Boone
County
area
came
from
the
southwest
and
typically
from
7­
10
knots.
(
See
figure
1­
A)
The
mean
high
temperature
for
July
for
the
area
from
1961
through
1990
was
86
°
F,
the
mean
low
was
65
°
F.
The
mean
precipitation
for
the
same
period
was
4.2
inches.

Planning
The
authority
for
air
quality
planning
in
the
Boone
County
area
resides
with
the
Kentucky
Natural
Resources
and
Environmental
Protection
Cabinet.
Transportation
planning
for
Boone
County
is
performed
by
the
Ohio,
Kentucky,
Indiana
Regional
Council
of
Governments
(
OKI).

Air
Monitoring
For
the
2000
 
2002
monitoring
period,
the
ozone
monitor
(
21­
015­
0003)
in
Boone
County,
shows
an
8­
hour
design
value
of
.086
which
would
be
classified
as
a
county
in
violation
of
the
standard.
(
See
table
1­
A)

Population
Based
on
projections
to
2001
from
the
2000
census
data,
there
are
90,489
persons
living
in
Boone
County.
That
represents
approximately
368
persons
per
square
mile.
The
population
of
Boone
County
is
approximately
25%
rural
with
3
the
remaining
75%
living
in
incorporated
areas.
The
largest
cities
in
Boone
County
are
Florence
and
Burlington.
(
See
table
1­
C)

Boone
County's
population
from
1990
through
2000
increased
by
approximately
49%
(
57,589
to
85,991).
The
population
is
further
expected
to
increase
by
an
additional
47%
between
2000
and
2010.
(
See
table
1­
B)

For
the
entire
Cincinnati­
Hamilton
MSA,
Boone
County
represents
approximately
5%
of
the
total
population
in
the
MSA
and
23%
of
the
Kentucky
portion
of
the
MSA.
(
See
table
1­
C)

Air
Emissions
The
graph
below
shows
point
source
VOC
emissions
from
Boone
County
were
estimated
at
2.61
tons
per
summer
day
(
tpsd)
in
2001
which
represents
approximately
59%
of
the
total
4.46
tpsd
of
overall
VOC
point
source
emissions
from
the
Kentucky
portion
of
the
Cincinnati­
Hamilton
MSA.
Point
source
NOx
emissions
from
Boone
County
were
estimated
at
21.57
tpsd
in
2001
which
represents
approximately
82%
of
the
total
26.29
tpsd
of
overall
NOx
point
source
emissions
from
the
Kentucky
portion
of
the
Cincinnati­
Hamilton
MSA.
(
See
table
1­
D)

A
comparison
across
the
entire
Ohio,
Kentucky,
Indiana
MSA
was
performed
using
the
federal
1999
National
Emission
Inventory
data.
Figures
1­
C
through
1­
F
provide
a
comparison
of
Boone
County's
emissions
to
the
entire
region.

2001
Point
Source
Emissions
Point
sources
located
within
Boone
County
are
subject
to
PSD
requirements,
CTG
RACT
requirements,
Maximum
Achievable
Control
Technology
(
MACT)
requirements
for
sources
of
Hazardous
Air
Pollutants,
and
New
Source
VOC
Emissions
tons
per
summer
day
Gallatin
10%

Grant
4%

Pendleton
6%
Kenton
13%

Boone
59%
Campbell
8%

NOx
Emissions
tons
per
summer
day
Gallatin
1%
Grant
0%

Pendleton
16%
Kenton
0%

Boone
82%
Campbell
1%
4
Performance
Standards
(
NSPS).
Any
controls
imposed
as
a
result
of
previous
nonattainment
designations
are
required
to
remain
in
Boone
County.

It
should
be
noted
that
three
emission
control
strategies
relating
to
onroad
mobile
sources
are
in
place
in
Boone
County:
a
vehicle
inspection
and
maintenance
program,
Stage
II
Vapor
Recovery
at
gasoline
pumps,
and
reformulated
gasoline.
Stage
I
controls
at
gasoline
stations
are
also
in
place
in
Boone
County.

Onroad
mobile
source
VOC
emissions
from
Boone
County
were
estimated
at
4.71
tpsd
in
2001
which
represents
approximately
29%
of
the
total
16.44
tpsd
of
overall
VOC
onroad
mobile
source
emissions
from
the
Kentucky
portion
of
the
Cincinnati­
Hamilton
MSA.
Onroad
mobile
source
NOx
emissions
from
Boone
County
were
estimated
at
11.58
tpsd
in
2001
which
represents
approximately
30%
of
the
total
38.12
tpsd
of
overall
NOx
onroad
mobile
source
emissions
from
the
Kentucky
portion
of
the
Cincinnati­
Hamilton
MSA.
(
See
table
1­
D)

A
comparison
across
the
entire
Ohio,
Kentucky,
Indiana
MSA
was
performed
using
the
federal
1999
National
Emission
Inventory
data.
Figures
1­
C
through
1­
F
provide
a
comparison
of
Boone
County's
emissions
to
the
entire
region.

2001
Onroad
Mobile
Source
Emissions
Commuting
traffic
from
other
counties
into
Boone
County
is
significant,
and
the
commuting
traffic
from
Boone
County
into
other
counties
is
high.

Commuting
Classifications
Not
Significant
0­
10%
Minimal
11­
30%
High
31­
50%
Significant
51%
or
more
VOC
Emissions
tons
per
summer
day
Kenton
29%
Gallatin
7%
Grant
15%
Pendleton
4%

Boone
29%

Campbell
16%

NOx
Emissions
tons
per
summer
day
Kenton
32%
Gallatin
6%
Grant
13%
Pendleton
2%

Boone
30%

Campbell
17%
5
2001
VOC
Contribution
(
tons
per
summer
day)

2001
NOx
Contribution
(
tons
per
summer
day)
2.61
4.71
0.37
2.59
0.43
1.14
0.18
2.51
0.59
4.77
0.28
0.72
0
2
4
6
8
10
Boone
Campbell
Gallatin
Grant
Kenton
Pendleton
Mobile
Point
21.57
11.58
0.15
6.37
0.30
2.39
0.00
5.13
0.03
11.71
4.24
0.94
0
5
10
15
20
25
30
35
Boone
Campbell
Gallatin
Grant
Kenton
Pendleton
Mobile
Point
6
Conclusion
and
Recommendation
The
monitoring
and
emissions
data
and
other
documentation
presented
indicate
that
Boone
County,
Kentucky,
does
contribute
a
significant
amount
of
ozone
forming
emissions
in
the
Kentucky
portion
of
the
area.
While
overall
VOC
emission
reductions
have
occurred
since
1990
in
the
area
with
a
required
15%
VOC
emission
reduction
plan
under
the
1­
hour
ozone
standard,
the
county
has
recorded
a
violation
of
the
8­
hour
ozone
standard
based
on
the
2000
 
2002
monitoring
data.
Therefore,
Boone
County
should
be
designated
nonattainment
for
the
8­
hour
ozone
standard.
7
CAMPBELL
COUNTY,
KENTUCKY
Campbell
County
is
part
of
the
Cincinnati­
Hamilton
Metropolitan
Statistical
Area
(
MSA)
and
is
located
to
the
east
of
Kenton
County,
Kentucky,
to
the
north
of
Pendleton
County,
Kentucky,
and
to
the
southeast
of
Cincinnati,
Ohio.

Geography/
Topography
Campbell
County
has
a
land
area
of
151
square
miles
and
is
located
on
the
banks
of
the
Ohio
River
in
the
tri­
state
area
of
Kentucky,
Ohio
and
Indiana.

Meteorological
Information
Wind
speed/
wind
direction
information
shows
that
the
majority
of
the
time
for
the
period
1988
 
1992,
the
wind
in
the
Campbell
County
area
came
from
the
southwest
and
typically
from
7­
10
knots.
(
See
figure
1­
A)
The
mean
high
temperature
for
July
for
the
area
from
1961
through
1990
was
86
°
F,
the
mean
low
was
65
°
F.
The
mean
precipitation
for
the
same
period
was
4.2
inches.

Planning
The
authority
for
air
quality
planning
in
the
Campbell
County
area
resides
with
the
Kentucky
Natural
Resources
and
Environmental
Protection
Cabinet.
Transportation
planning
for
Campbell
County
is
performed
by
the
Ohio,
Kentucky,
Indiana
Regional
Council
of
Governments
(
OKI).

Air
Monitoring
For
the
2000
 
2002
monitoring
period,
the
ozone
monitor
(
21­
037­
1001)
in
Campbell
County,
shows
an
8­
hour
design
value
of
.094
which
would
be
classified
as
a
county
in
violation
of
the
standard.
(
See
table
1­
A)

Population
Based
on
projections
to
2001
from
the
2000
census
data,
there
are
88,362
persons
living
in
Campbell
County.
That
represents
approximately
585
persons
per
square
mile.
The
population
of
Campbell
County
is
approximately
16%
rural
with
the
remaining
84%
living
in
incorporated
areas.
The
largest
cities
in
Campbell
County
are
Newport
and
Ft.
Thomas.
(
See
table
1­
C)
8
Campbell
County's
population
from
1990
through
2000
increased
by
approximately
6%
(
83,866
to
88,616).
The
population
is
further
expected
to
increase
by
an
additional
4%
between
2000
and
2010.
(
See
table
1­
B)

For
the
entire
Cincinnati­
Hamilton
MSA,
Campbell
County
represents
approximately
4%
of
the
total
population
in
the
MSA
and
24%
of
the
Kentucky
portion
of
the
MSA.
(
See
table
1­
C)

Air
Emissions
Point
source
VOC
emissions
from
Campbell
County
were
estimated
at
0.37
tpsd
in
2001
which
represents
approximately
8%
of
the
total
4.46
tpsd
of
overall
VOC
point
source
emissions
from
the
Kentucky
portion
of
the
Cincinnati­
Hamilton
MSA.
Point
source
NOx
emissions
from
Campbell
County
were
estimated
at
0.15
tpsd
in
2001
which
represents
approximately
1%
of
the
total
26.29
tpsd
of
overall
NOx
point
source
emissions
from
the
Kentucky
portion
of
the
Cincinnati­
Hamilton
MSA.
(
See
table
1­
D)

A
comparison
across
the
entire
Ohio,
Kentucky,
Indiana
MSA
was
performed
using
the
federal
1999
National
Emission
Inventory
data.
Figures
1­
C
through
1­
F
provide
a
comparison
of
Campbell
County's
emissions
to
the
entire
region.

2001
Point
Source
Emissions
Point
sources
located
within
Campbell
County
are
subject
to
PSD
requirements,
CTG
RACT
requirements,
Maximum
Achievable
Control
Technology
(
MACT)
requirements
for
sources
of
Hazardous
Air
Pollutants,
and
New
Source
Performance
Standards
(
NSPS).
Any
controls
imposed
as
a
result
of
previous
nonattainment
designations
are
required
to
remain
in
Campbell
County.
NOx
Emissions
tons
per
summer
day
Gallatin
1%
Grant
0%

Pendleton
16%
Kenton
0%

Boone
82%
Campbell
1%

VOC
Emissions
tons
per
summer
day
Gallatin
10%

Grant
4%

Pendleton
6%
Kenton
13%

Boone
59%
Campbell
8%
9
It
should
be
noted
that
three
emission
control
strategies
relating
to
onroad
mobile
sources
are
in
place
in
Campbell
County:
a
vehicle
inspection
and
maintenance
program,
Stage
II
Vapor
Recovery,
and
reformulated
gasoline.
Stage
I
controls
at
gasoline
stations
are
also
in
place
in
Campbell
County.

Onroad
mobile
source
VOC
emissions
from
Campbell
County
were
estimated
at
2.59
tpsd
in
2001
which
represents
approximately
16%
of
the
total
16.44
tpsd
of
overall
VOC
onroad
mobile
source
emissions
from
the
Kentucky
portion
of
the
Cincinnati­
Hamilton
MSA.
Onroad
mobile
source
NOx
emissions
from
Campbell
County
were
estimated
at
6.37
tpsd
in
2001
which
represents
approximately
17%
of
the
total
38.12
tpsd
of
overall
NOx
onroad
mobile
source
emissions
from
the
Kentucky
portion
of
the
Cincinnati­
Hamilton
MSA.
(
See
table
1­
D)

A
comparison
across
the
entire
Ohio,
Kentucky,
Indiana
MSA
was
performed
using
the
federal
1999
National
Emission
Inventory
data.
Figures
1­
C
through
1­
F
provide
a
comparison
of
Campbell
County's
emissions
to
the
entire
region.

2001
Onroad
Mobile
Source
Emissions
Commuting
traffic
from
other
counties
into
Campbell
County
is
high,
and
the
commuting
traffic
from
Campbell
County
into
other
counties
is
significant.

Commuting
Classifications
Not
Significant
0­
10%
Minimal
11­
30%
High
31­
50%
Significant
51%
or
more
VOC
Emissions
tons
per
summer
day
Kenton
29%
Gallatin
7%
Grant
15%
Pendleton
4%

Boone
29%

Campbell
16%

NOx
Emissions
tons
per
summer
day
Kenton
32%
Gallatin
6%
Grant
13%
Pendleton
2%

Boone
30%

Campbell
17%
10
2001
VOC
Contribution
(
tons
per
summer
day)

2001
NOx
Contribution
(
tons
per
summer
day)
2.61
4.71
0.37
2.59
0.43
1.14
0.18
2.51
0.59
4.77
0.28
0.72
0
2
4
6
8
10
Boone
Campbell
Gallatin
Grant
Kenton
Pendleton
Mobile
Point
21.57
11.58
0.15
6.37
0.30
2.39
0.00
5.13
0.03
11.71
4.24
0.94
0
5
10
15
20
25
30
35
Boone
Campbell
Gallatin
Grant
Kenton
Pendleton
Mobile
Point
11
Conclusion
and
Recommendation
The
monitoring
and
emissions
data
and
other
documentation
presented
indicate
that
Campbell
County,
Kentucky,
does
contribute
ozone
forming
emissions
in
the
area.
While
overall
VOC
emission
reductions
have
occurred
since
1990
in
the
area
with
a
required
15%
VOC
emission
reduction
plan
under
the
1­
hour
ozone
standard,
the
county
has
recorded
a
violation
of
the
8­
hour
ozone
standard
based
on
the
2000
 
2002
monitoring
data.
Therefore,
Campbell
County
should
be
designated
nonattainment
for
the
8­
hour
ozone
standard.
12
KENTON
COUNTY,
KENTUCKY
Kenton
County
is
part
of
the
Cincinnati­
Hamilton
Metropolitan
Statistical
Area
(
MSA)
and
is
located
to
the
west
of
Campbell
County,
Kentucky,
to
the
east
of
Boone
County,
Kentucky,
and
to
the
south
of
Cincinnati,
Ohio.

Geography/
Topography
Kenton
County
has
a
land
area
of
162
square
miles
and
is
located
on
the
banks
of
the
Ohio
River
in
the
tri­
state
area
of
Kentucky,
Ohio
and
Indiana.

Meteorological
Information
Wind
speed/
wind
direction
information
shows
that
the
majority
of
the
time
for
the
period
1988
 
1992,
the
wind
in
the
Kenton
County
area
came
from
the
southwest
and
typically
from
7­
10
knots.
(
See
figure
1­
A)
The
mean
high
temperature
for
July
for
the
area
from
1961
through
1990
was
86
°
F,
the
mean
low
was
65
°
F.
The
mean
precipitation
for
the
same
period
was
4.2
inches.

Planning
The
authority
for
air
quality
planning
in
the
Kenton
County
area
resides
with
the
Kentucky
Natural
Resources
and
Environmental
Protection
Cabinet.
Transportation
planning
for
Kenton
County
is
performed
by
the
Ohio,
Kentucky,
Indiana
Regional
Council
of
Governments
(
OKI).

Air
Monitoring
For
the
2000
 
2002
monitoring
period,
the
ozone
monitor
(
21­
117­
0007)
in
Kenton
County,
shows
an
8­
hour
design
value
of
.088
which
would
be
classified
as
a
county
in
violation
of
the
standard.
(
See
table
1­
A)

Population
Based
on
projections
to
2001
from
the
2000
census
data,
there
are
151,366
persons
living
in
Kenton
County.
That
represents
approximately
934
persons
per
square
mile.
The
population
of
Kenton
County
is
approximately
7%
rural
with
the
remaining
93%
living
in
incorporated
areas.
The
largest
cities
in
Kenton
County
are
Covington
and
Erlanger.
(
See
table
1­
C)
13
Kenton
County's
population
from
1990
through
2000
increased
by
approximately
7%
(
142,031
to
151,464).
The
population
is
further
expected
to
increase
by
an
additional
6%
between
2000
and
2010.
(
See
table
1­
B)

For
the
entire
Cincinnati­
Hamilton
MSA,
Kenton
County
represents
approximately
8%
of
the
total
population
in
the
MSA
and
40%
of
the
Kentucky
portion
of
the
MSA.
(
See
table
1­
C)

Air
Emissions
Point
source
VOC
emissions
from
Kenton
County
were
estimated
at
0.59
tpsd
in
2001
which
represents
approximately
13%
of
the
total
4.46
tpsd
of
overall
VOC
point
source
emissions
from
the
Kentucky
portion
of
the
Cincinnati­
Hamilton
MSA.
Point
source
NOx
emissions
from
Kenton
County
were
estimated
at
0.03
tpsd
in
2001
which
represents
less
than
1%
of
the
total
26.29
tpsd
of
overall
NOx
point
source
emissions
from
the
Kentucky
portion
of
the
Cincinnati­
Hamilton
MSA.
(
See
table
1­
D)

A
comparison
across
the
entire
Ohio,
Kentucky,
Indiana
MSA
was
performed
using
the
federal
1999
National
Emission
Inventory
data.
Figures
1­
C
through
1­
F
provide
a
comparison
of
Kenton
County's
emissions
to
the
entire
region.

2001
Point
Source
Emissions
Point
sources
located
within
Kenton
County
are
subject
to
PSD
requirements,
CTG
RACT
requirements,
Maximum
Achievable
Control
Technology
(
MACT)
requirements
for
sources
of
Hazardous
Air
Pollutants,
and
New
Source
Performance
Standards
(
NSPS).
Any
controls
imposed
as
a
result
of
previous
nonattainment
designations
are
required
to
remain
in
Kenton
County.
NOx
Emissions
tons
per
summer
day
Gallatin
1%
Grant
0%

Pendleton
16%
Kenton
0%

Boone
82%
Campbell
1%

VOC
Emissions
tons
per
summer
day
Gallatin
10%

Grant
4%

Pendleton
6%
Kenton
13%

Boone
59%
Campbell
8%
14
It
should
be
noted
that
three
emission
control
strategies
relating
to
onroad
mobile
sources
are
in
place
in
Kenton
County:
a
vehicle
inspection
and
maintenance
program,
Stage
II
Vapor
Recovery,
and
reformulated
gasoline.
Stage
I
controls
at
gasoline
stations
are
also
in
place
in
Kenton
County.

Onroad
mobile
source
VOC
emissions
from
Kenton
County
were
estimated
at
4.77
tpsd
in
2001
which
represents
approximately
29%
of
the
total
16.44
tpsd
of
overall
VOC
onroad
mobile
source
emissions
from
the
Kentucky
portion
of
the
Cincinnati­
Hamilton
MSA.
Onroad
mobile
source
NOx
emissions
from
Kenton
County
were
estimated
at
11.71
tpsd
in
2001
which
represents
approximately
32%
of
the
total
38.12
tpsd
of
overall
NOx
onroad
mobile
source
emissions
from
the
Kentucky
portion
of
the
Cincinnati­
Hamilton
MSA.
(
See
table
1­
D)

A
comparison
across
the
entire
Ohio,
Kentucky,
Indiana
MSA
was
performed
using
the
federal
1999
National
Emission
Inventory
data.
Figures
1­
C
through
1­
F
provide
a
comparison
of
Kenton
County's
emissions
to
the
entire
region.

2001
Onroad
Mobile
Source
Emissions
Commuting
traffic
from
other
counties
into
Kenton
County
is
high,
and
the
commuting
traffic
from
Kenton
County
into
other
counties
is
significant.

Commuting
Classifications
Not
Significant
0­
10%
Minimal
11­
30%
High
31­
50%
Significant
51%
or
more
VOC
Emissions
tons
per
summer
day
Kenton
29%
Gallatin
7%
Grant
15%
Pendleton
4%

Boone
29%

Campbell
16%

NOx
Emissions
tons
per
summer
day
Kenton
32%
Gallatin
6%
Grant
13%
Pendleton
2%

Boone
30%

Campbell
17%
15
2001
VOC
Contribution
(
tons
per
summer
day)

2001
NOx
Contribution
(
tons
per
summer
day)
2.61
4.71
0.37
2.59
0.43
1.14
0.18
2.51
0.59
4.77
0.28
0.72
0
2
4
6
8
10
Boone
Campbell
Gallatin
Grant
Kenton
Pendleton
Mobile
Point
21.57
11.58
0.15
6.37
0.30
2.39
0.00
5.13
0.03
11.71
4.24
0.94
0
5
10
15
20
25
30
35
Boone
Campbell
Gallatin
Grant
Kenton
Pendleton
Mobile
Point
16
Conclusion
and
Recommendation
The
monitoring
and
emissions
data
and
other
documentation
presented
indicate
that
Kenton
County,
Kentucky,
does
contribute
ozone
forming
emissions
in
the
area.
While
overall
VOC
emission
reductions
have
occurred
since
1990
in
the
area
with
a
required
15%
VOC
emission
reduction
plan
under
the
1­
hour
ozone
standard,
the
county
has
recorded
a
violation
of
the
8­
hour
ozone
standard
based
on
the
2000
 
2002
monitoring
data.
Therefore,
Kenton
County
should
be
designated
nonattainment
for
the
8­
hour
ozone
standard.
17
GALLATIN
COUNTY,
KENTUCKY
Gallatin
County
is
part
of
the
Cincinnati­
Hamilton
Metropolitan
Statistical
Area
(
MSA)
and
is
located
to
the
southwest
of
Boone
County,
Kentucky,
and
to
the
northwest
of
Owen
and
Grant
Counties,
Kentucky.

Geography/
Topography
Gallatin
County
has
a
land
area
of
98
square
miles
and
is
located
on
the
banks
of
the
Ohio
River
in
the
tri­
state
area
of
Kentucky,
Ohio
and
Indiana.

Meteorological
Information
Wind
speed/
wind
direction
information
shows
that
the
majority
of
the
time
for
the
period
1988
 
1992,
the
wind
in
the
Gallatin
County
area
came
from
the
southwest
and
typically
from
7­
10
knots.
(
See
figure
1­
A)
The
mean
high
temperature
for
July
for
the
area
from
1961
through
1990
was
86
°
F,
the
mean
low
was
65
°
F.
The
mean
precipitation
for
the
same
period
was
4.2
inches.

Planning
The
authority
for
air
quality
planning
in
the
Gallatin
County
area
resides
with
the
Kentucky
Natural
Resources
and
Environmental
Protection
Cabinet.
Transportation
planning
for
Gallatin
County
is
performed
by
the
Kentucky
Transportation
Cabinet.

Air
Monitoring
For
the
2000
 
2002
monitoring
period,
there
were
no
ozone
monitors
located
in
Gallatin
County.
However,
the
Boone,
Kenton,
and
Campbell
County
monitors
to
the
north
and
northeast
all
show
8­
hour
design
values
in
exceedance
of
the
National
Ambient
Air
Quality
Standards
(
NAAQS).
(
See
table
1­
A)

Population
Based
on
projections
to
2001
from
the
2000
census
data,
there
are
7,961
persons
living
in
Gallatin
County.
That
represents
approximately
81
persons
per
square
mile.
The
population
of
Gallatin
County
is
approximately
100%
rural
18
with
few
people
living
in
incorporated
areas.
The
largest
cities
in
Gallatin
County
are
Warsaw
and
Glencoe.
(
See
table
1­
C)

Gallatin
County's
population
from
1990
through
2000
increased
by
approximately
46%
(
5,393
to
7,870).
The
population
is
further
expected
to
increase
by
an
additional
48%
between
2000
and
2010.
(
See
table
1­
B)

For
the
entire
Cincinnati­
Hamilton
MSA,
Gallatin
County
represents
less
than
1%
of
the
total
population
in
the
MSA
and
2%
of
the
Kentucky
portion
of
the
MSA.
(
See
table
1­
C)

Air
Emissions
Point
source
VOC
emissions
from
Gallatin
County
were
estimated
at
0.43
tpsd
in
2001
which
represents
approximately
10%
of
the
total
4.46
tpsd
of
overall
VOC
point
source
emissions
from
the
Kentucky
portion
of
the
Cincinnati­
Hamilton
MSA.
Point
source
NOx
emissions
from
Gallatin
County
were
estimated
at
0.30
tpsd
in
2001
which
represents
approximately
1%
of
the
total
26.29
tpsd
of
overall
NOx
point
source
emissions
from
the
Kentucky
portion
of
the
Cincinnati­
Hamilton
MSA.
(
See
table
1­
D)

A
comparison
across
the
entire
Ohio,
Kentucky,
Indiana
MSA
was
performed
using
the
federal
1999
National
Emission
Inventory
data.
Figures
1­
C
through
1­
F
provide
a
comparison
of
Gallatin
County's
emissions
to
the
entire
region.

2001
Point
Source
Emissions
Point
sources
located
within
Gallatin
County
are
subject
to
PSD
requirements,
CTG
RACT
requirements,
Maximum
Achievable
Control
Technology
(
MACT)
requirements
for
sources
of
Hazardous
Air
Pollutants,
and
New
Source
Performance
Standards
(
NSPS).
NOx
Emissions
tons
per
summer
day
Gallatin
1%
Grant
0%

Pendleton
16%
Kenton
0%

Boone
82%
Campbell
1%

VOC
Emissions
tons
per
summer
day
Gallatin
10%

Grant
4%

Pendleton
6%
Kenton
13%

Boone
59%
Campbell
8%
19
Onroad
mobile
source
VOC
emissions
from
Gallatin
County
were
estimated
at
1.14
tpsd
in
2001
which
represents
approximately
7%
of
the
total
16.44
tpsd
of
overall
VOC
onroad
mobile
source
emissions
from
the
Kentucky
portion
of
the
Cincinnati­
Hamilton
MSA.
Onroad
mobile
source
NOx
emissions
from
Gallatin
County
were
estimated
at
2.39
tpsd
in
2001
which
represents
approximately
6%
of
the
total
38.12
tpsd
of
overall
NOx
onroad
mobile
source
emissions
from
the
Kentucky
portion
of
the
Cincinnati­
Hamilton
MSA.
(
See
table
1­
D)

A
comparison
across
the
entire
Ohio,
Kentucky,
Indiana
MSA
was
performed
using
the
federal
1999
National
Emission
Inventory
data.
Figures
1­
C
through
1­
F
provide
a
comparison
of
Gallatin
County's
emissions
to
the
entire
region.

2001
Onroad
Mobile
Source
Emissions
Commuting
traffic
from
other
counties
into
Gallatin
County
is
high,
and
the
commuting
traffic
from
Gallatin
County
into
other
counties
is
significant.

Commuting
Classifications
Not
Significant
0­
10%
Minimal
11­
30%
High
31­
50%
Significant
51%
or
more
VOC
Emissions
tons
per
summer
day
Kenton
29%
Gallatin
7%
Grant
15%
Pendleton
4%

Boone
29%

Campbell
16%

NOx
Emissions
tons
per
summer
day
Kenton
32%
Gallatin
6%
Grant
13%
Pendleton
2%

Boone
30%

Campbell
17%
20
2001
VOC
Contribution
(
tons
per
summer
day)

2001
NOx
Contribution
(
tons
per
summer
day)
2.61
4.71
0.37
2.59
0.43
1.14
0.18
2.51
0.59
4.77
0.28
0.72
0
2
4
6
8
10
Boone
Campbell
Gallatin
Grant
Kenton
Pendleton
Mobile
Point
21.57
11.58
0.15
6.37
0.30
2.39
0.00
5.13
0.03
11.71
4.24
0.94
0
5
10
15
20
25
30
35
Boone
Campbell
Gallatin
Grant
Kenton
Pendleton
Mobile
Point
21
Conclusion
and
Recommendation
The
emissions
data
and
other
documentation
presented
indicate
that
Gallatin
County,
Kentucky,
does
not
contribute
significantly
to
the
monitored
violations
in
the
region
and
therefore
should
be
designated
attainment
for
the
8­
hour
ozone
standard.
22
GRANT
COUNTY,
KENTUCKY
Grant
County
is
part
of
the
Cincinnati­
Hamilton
Metropolitan
Statistical
Area
(
MSA)
and
is
located
to
the
southeast
of
Gallatin
County,
Kentucky,
to
the
west
of
Pendleton
County,
Kentucky,
and
directly
north
of
Scott
County,
Kentucky.

Geography/
Topography
Grant
County
has
a
land
area
of
259
square
miles
and
is
located
in
the
tri­
state
area
of
Kentucky,
Ohio
and
Indiana.

Meteorological
Information
Wind
speed/
wind
direction
information
shows
that
the
majority
of
the
time
for
the
period
1988
 
1992,
the
wind
in
the
Grant
County
area
came
from
the
southwest
and
typically
from
7­
10
knots.
(
See
figure
1­
A)
The
mean
high
temperature
for
July
for
the
area
from
1961
through
1990
was
86
°
F,
the
mean
low
was
65
°
F.
The
mean
precipitation
for
the
same
period
was
4.2
inches.

Planning
The
authority
for
air
quality
planning
in
the
Grant
County
area
resides
with
the
Kentucky
Natural
Resources
and
Environmental
Protection
Cabinet.
Transportation
planning
for
Grant
County
is
performed
by
the
Kentucky
Transportation
Cabinet.

Air
Monitoring
For
the
2000
 
2002
monitoring
period,
there
were
no
ozone
monitors
located
in
Grant
County.
However,
the
Boone,
Kenton,
and
Campbell
County
monitors
to
the
northwest,
north,
and
northeast
all
show
8­
hour
design
values
in
exceedance
of
the
National
Ambient
Air
Quality
Standards
(
NAAQS).
(
See
table
1­
A)

Population
Based
on
projections
to
2001
from
the
2000
census
data,
there
are
23,237
persons
living
in
Grant
County.
That
represents
approximately
90
persons
per
square
mile.
The
population
of
Grant
County
is
approximately
78%
rural
with
23
the
remaining
22%
living
in
incorporated
areas.
The
largest
cities
in
Grant
County
are
Williamstown
and
Dry
Ridge.
(
See
table
1­
C)

Grant
County's
population
from
1990
through
2000
increased
by
approximately
42%
(
15,737
to
22,384).
The
population
is
further
expected
to
increase
by
an
additional
45%
between
2000
and
2010.
(
See
table
1­
B)

For
the
entire
Cincinnati­
Hamilton
MSA,
Grant
County
represents
approximately
1%
of
the
total
population
in
the
MSA
and
6%
of
the
Kentucky
portion
of
the
MSA.
(
See
table
1­
C)

Air
Emissions
Point
source
VOC
emissions
from
Grant
County
were
estimated
at
0.18
tpsd
in
2001
which
represents
approximately
4%
of
the
total
4.46
tpsd
of
overall
VOC
point
source
emissions
from
the
Kentucky
portion
of
the
Cincinnati­
Hamilton
MSA.
Point
source
NOx
emissions
from
Grant
County
were
estimated
at
0.00
tpsd
in
2001
which
represents
0%
of
the
total
26.29
tpsd
of
overall
NOx
point
source
emissions
from
the
Kentucky
portion
of
the
Cincinnati­
Hamilton
MSA.
(
See
table
1­
D)

A
comparison
across
the
entire
Ohio,
Kentucky,
Indiana
MSA
was
performed
using
the
federal
1999
National
Emission
Inventory
data.
Figures
1­
C
through
1­
F
provide
a
comparison
of
Grant
County's
emissions
to
the
entire
region.

2001
Point
Source
Emissions
Point
sources
located
within
Grant
County
are
subject
to
PSD
requirements,
CTG
RACT
requirements,
Maximum
Achievable
Control
Technology
(
MACT)
requirements
for
sources
of
Hazardous
Air
Pollutants,
and
New
Source
Performance
Standards
(
NSPS).
NOx
Emissions
tons
per
summer
day
Gallatin
1%
Grant
0%

Pendleton
16%
Kenton
0%

Boone
82%
Campbell
1%

VOC
Emissions
tons
per
summer
day
Gallatin
10%

Grant
4%

Pendleton
6%
Kenton
13%

Boone
59%
Campbell
8%
24
Onroad
mobile
source
VOC
emissions
from
Grant
County
were
estimated
at
2.51
tpsd
in
2001
which
represents
approximately
15%
of
the
total
16.44
tpsd
of
overall
VOC
onroad
mobile
source
emissions
from
the
Kentucky
portion
of
the
Cincinnati­
Hamilton
MSA.
Onroad
mobile
source
NOx
emissions
from
Grant
County
were
estimated
at
5.13
tpsd
in
2001
which
represents
approximately
13%
of
the
total
38.12
tpsd
of
overall
NOx
onroad
mobile
source
emissions
from
the
Kentucky
portion
of
the
Cincinnati­
Hamilton
MSA.
(
See
table
1­
D)

A
comparison
across
the
entire
Ohio,
Kentucky,
Indiana
MSA
was
performed
using
the
federal
1999
National
Emission
Inventory
data.
Figures
1­
C
through
1­
F
provide
a
comparison
of
Grant
County's
emissions
to
the
entire
region.

2001
Onroad
Mobile
Source
Emissions
Commuting
traffic
from
other
counties
into
Grant
County
is
minimal,
and
the
commuting
traffic
from
Grant
County
into
other
counties
is
significant.

Commuting
Classifications
Not
Significant
0­
10%
Minimal
11­
30%
High
31­
50%
Significant
51%
or
more
VOC
Emissions
tons
per
summer
day
Kenton
29%
Gallatin
7%
Grant
15%
Pendleton
4%

Boone
29%

Campbell
16%

NOx
Emissions
tons
per
summer
day
Kenton
32%
Gallatin
6%
Grant
13%
Pendleton
2%

Boone
30%

Campbell
17%
25
2001
VOC
Contribution
(
tons
per
summer
day)

2001
NOx
Contribution
(
tons
per
summer
day)
2.61
4.71
0.37
2.59
0.43
1.14
0.18
2.51
0.59
4.77
0.28
0.72
0
2
4
6
8
10
Boone
Campbell
Gallatin
Grant
Kenton
Pendleton
Mobile
Point
21.57
11.58
0.15
6.37
0.30
2.39
0.00
5.13
0.03
11.71
4.24
0.94
0
5
10
15
20
25
30
35
Boone
Campbell
Gallatin
Grant
Kenton
Pendleton
Mobile
Point
26
Conclusion
and
Recommendation
The
emissions
data
and
other
documentation
presented
indicate
that
Grant
County,
Kentucky,
does
not
contribute
significantly
to
the
monitored
violations
in
the
region
and
therefore
should
be
designated
attainment
for
the
8­
hour
ozone
standard.
27
PENDLETON
COUNTY,
KENTUCKY
Pendleton
County
is
part
of
the
Cincinnati­
Hamilton
Metropolitan
Statistical
Area
(
MSA)
and
is
located
directly
south
of
Kenton
and
Campbell
Counties,
Kentucky,
and
to
the
east
of
Grant
County,
Kentucky.

Geography/
Topography
Pendleton
County
has
a
land
area
of
280
square
miles
and
is
located
on
the
banks
of
the
Ohio
River
in
the
tri­
state
area
of
Kentucky,
Ohio
and
Indiana.

Meteorological
Information
Wind
speed/
wind
direction
information
shows
that
the
majority
of
the
time
for
the
period
1988
 
1992,
the
wind
in
the
Pendleton
County
area
came
from
the
southwest
and
typically
from
7­
10
knots.
(
See
figure
1­
A)
The
mean
high
temperature
for
July
for
the
area
from
1961
through
1990
was
86
°
F,
the
mean
low
was
65
°
F.
The
mean
precipitation
for
the
same
period
was
4.2
inches.

Planning
The
authority
for
air
quality
planning
in
the
Pendleton
County
area
resides
with
the
Kentucky
Natural
Resources
and
Environmental
Protection
Cabinet.
Transportation
planning
for
Pendleton
County
is
performed
by
the
Kentucky
Transportation
Cabinet.

Air
Monitoring
For
the
2000
 
2002
monitoring
period,
there
were
no
ozone
monitors
located
in
Pendleton
County.
However,
the
Boone,
Kenton,
and
Campbell
County
monitors
to
the
north
and
northwest
all
show
8­
hour
design
values
in
exceedance
of
the
National
Ambient
Air
Quality
Standards
(
NAAQS).
(
See
table
1­
A)

Population
Based
on
projections
to
2001
from
the
2000
census
data,
there
are
14,611
persons
living
in
Pendleton
County.
That
represents
approximately
52
persons
per
square
mile.
The
population
of
Pendleton
County
is
approximately
100%
28
rural
with
few
people
living
in
incorporated
areas.
The
largest
cities
in
Pendleton
County
are
Falmouth
and
Butler.
(
See
table
1­
C)

Pendleton
County's
population
from
1990
through
2000
increased
by
approximately
20%
(
12,036
to
14,390).
The
population
is
further
expected
to
increase
by
an
additional
23%
between
2000
and
2010.
(
See
table
1­
B)

For
the
entire
Cincinnati­
Hamilton
MSA,
Pendleton
County
represents
approximately
1%
of
the
total
population
in
the
MSA
and
4%
of
the
Kentucky
portion
of
the
MSA.
(
See
table
1­
C)

Air
Emissions
Point
source
VOC
emissions
from
Pendleton
County
were
estimated
at
0.28
tpsd
in
2001
which
represents
approximately
6%
of
the
total
4.46
tpsd
of
overall
VOC
point
source
emissions
from
the
Kentucky
portion
of
the
Cincinnati­
Hamilton
MSA.
Point
source
NOx
emissions
from
Pendleton
County
were
estimated
at
4.24
tpsd
in
2001
which
represents
approximately
16%
of
the
total
26.29
tpsd
of
overall
NOx
point
source
emissions
from
the
Kentucky
portion
of
the
Cincinnati­
Hamilton
MSA.
(
See
table
1­
D)

A
comparison
across
the
entire
Ohio,
Kentucky,
Indiana
MSA
was
performed
using
the
federal
1999
National
Emission
Inventory
data.
Figures
1­
C
through
1­
F
provide
a
comparison
of
Pendleton
County's
emissions
to
the
entire
region.

2001
Point
Source
Emissions
Point
sources
located
within
Pendleton
County
are
subject
to
PSD
requirements,
CTG
RACT
requirements,
Maximum
Achievable
Control
NOx
Emissions
tons
per
summer
day
Gallatin
1%
Grant
0%

Pendleton
16%
Kenton
0%

Boone
82%
Campbell
1%

VOC
Emissions
tons
per
summer
day
Gallatin
10%

Grant
4%

Pendleton
6%
Kenton
13%

Boone
59%
Campbell
8%
29
Technology
(
MACT)
requirements
for
sources
of
Hazardous
Air
Pollutants,
and
New
Source
Performance
Standards
(
NSPS).

Onroad
mobile
source
VOC
emissions
from
Pendleton
County
were
estimated
at
0.72
tpsd
in
2001
which
represents
approximately
4%
of
the
total
16.44
tpsd
of
overall
VOC
onroad
mobile
source
emissions
from
the
Kentucky
portion
of
the
Cincinnati­
Hamilton
MSA.
Onroad
mobile
source
NOx
emissions
from
Pendleton
County
were
estimated
at
0.94
tpsd
in
2001
which
represents
approximately
2%
of
the
total
38.12
tpsd
of
overall
NOx
onroad
mobile
source
emissions
from
the
Kentucky
portion
of
the
Cincinnati­
Hamilton
MSA.
(
See
table
1­
D)

A
comparison
across
the
entire
Ohio,
Kentucky,
Indiana
MSA
was
performed
using
the
federal
1999
National
Emission
Inventory
data.
Figures
1­
C
through
1­
F
provide
a
comparison
of
Pendleton
County's
emissions
to
the
entire
region.

2001
Onroad
Mobile
Source
Emissions
Commuting
traffic
from
other
counties
into
Pendleton
County
is
minimal,
and
the
commuting
traffic
from
Pendleton
County
into
other
counties
is
significant.

Commuting
Classifications
Not
Significant
0­
10%
Minimal
11­
30%
High
31­
50%
Significant
51%
or
more
VOC
Emissions
tons
per
summer
day
Kenton
29%
Gallatin
7%
Grant
15%
Pendleton
4%

Boone
29%

Campbell
16%

NOx
Emissions
tons
per
summer
day
Kenton
32%
Gallatin
6%
Grant
13%
Pendleton
2%

Boone
30%

Campbell
17%
30
2001
VOC
Contribution
(
tons
per
summer
day)

2001
NOx
Contribution
(
tons
per
summer
day)
2.61
4.71
0.37
2.59
0.43
1.14
0.18
2.51
0.59
4.77
0.28
0.72
0
2
4
6
8
10
Boone
Campbell
Gallatin
Grant
Kenton
Pendleton
Mobile
Point
21.57
11.58
0.15
6.37
0.30
2.39
0.00
5.13
0.03
11.71
4.24
0.94
0
5
10
15
20
25
30
35
Boone
Campbell
Gallatin
Grant
Kenton
Pendleton
Mobile
Point
31
Conclusion
and
Recommendation
The
emissions
data
and
other
documentation
presented
indicate
that
Pendleton
County,
Kentucky,
does
not
contribute
significantly
to
the
monitored
violations
in
the
region
and
therefore
should
be
designated
attainment
for
the
8­
hour
ozone
standard.
32
Cincinnati­
Hamiltion
MSA
Figure
1­
A
Wind
Rose
Patterns
Figure
1­
B
2001
VOC
and
NOx
Emissions
Kentucky
Portion
of
the
Cincinnati­
Hamilton
MSA
(
tons
per
summer
day)

7.32
33.15
2.96
6.52
1.57
2.69
2.69
5.13
5.36
11.74
1.00
5.18
0
5
10
15
20
25
30
35
Boone
Campbell
Gallatin
Grant
Kenton
Pendleton
VOC
NOx
33
Table
1­
A
Ozone
Design
Values
(
parts
per
million)

Monitor
2000
2001
2002
3­
year
Average
Boone
.083
.083
.094
.086
Campbell
.093
.088
.102
.094
Kenton
.087
.082
.096
.088
Table
1­
B
Northern
Kentucky
Area
Population
Growth
Data
County
1990
2000
%
Growth
1990
 
2000
2010
%
Growth
2000
­
2010
Boone
57,589
85,991
49.3%
126,036
46.6%
Campbell
83,866
88,616
5.7%
92,385
4.3%
Gallatin
5,393
7,870
45.9%
11,638
47.9%
Grant
15,737
22,384
42.2%
32,341
44.5%
Kenton
142,031
151,464
6.6%
159,730
5.5%
Pendleton
12,036
14,390
19.6%
17,690
22.9%

Table
1­
C
2001
Estimated
Cincinnati­
Hamilton
MSA
Population
Kentucky
Estimated
Population
Boone
County
90,489
Campbell
County
88,362
Gallatin
County
7,961
Grant
County
23,237
Kenton
County
151,366
Pendleton
County
14,611
Ohio
Brown
County
42,890
Clermont
County
181,673
Hamilton
County
835,362
Butler
337,013
Warren
County
169,025
Indiana
Dearborn
County
46,806
Ohio
County
5,726
Total
Estimated
Population
1,994,521
34
Table
1­
D
2001
VOC
and
NOx
Emissions
(
tons
per
summer
day)

VOC
NOx
County
Point
Mobile
Total
Point
Mobile
Total
Boone
2.61
4.71
7.32
21.57
11.58
33.15
Campbell
0.37
2.59
2.96
0.15
6.37
6.52
Gallatin
0.43
1.14
1.57
0.30
2.39
2.69
Grant
0.18
2.51
2.69
0.00
5.13
5.13
Kenton
0.59
4.77
5.36
0.03
11.71
11.74
Pendleton
0.28
0.72
1.00
4.24
0.94
5.18
Total
4.46
16.44
20.90
26.29
38.12
64.41
Figure
1­
C
1999
NEI
Point
Source
VOC
Emissions
for
Cincinnati­
Hamilton
Area
tons
per
year
Grant
1%
Gallatin
2%
Ohio
0%
Brown
1%
Clermont
4%

Dearborn
14%
Butler
23%
Warren
4%
Hamilton
28%

Pendleton
2%
Kenton
5%
Boone
13%

Campbell
3%
35
Figure
1­
D
1999
NEI
Point
Source
NOx
Emissions
for
Cincinnati­
Hamilton
Area
tons
per
year
Grant
0%
Gallatin
0%
Ohio
0%

Brown
0%
Clermont
33%

Dearborn
27%
Butler
7%
Warren
1%
Hamilton
23%

Pendleton
1%
Kenton
0%
Boone
8%

Campbell
0%

Figure
1­
E
1999
NEI
Onroad
Mobile
Source
VOC
Emissions
for
Cincinnati­
Hamilton
Area
tons
per
year
Campbell
5%
Boone
4%

Kenton
9%
Pendleton
1%
Hamilton
44%
Warren
7%

Butler
14%

Dearborn
3%
Clermont
8%

Brown
2%

Ohio
0%
Gallatin
1%
Grant
2%
36
Figure
1­
F
1999
NEI
Onroad
Mobile
Source
NOx
Emissions
for
Cincinnati­
Hamilton
Area
tons
per
year
Campbell
6%
Boone
5%

Kenton
9%

Pendleton
1%
Hamilton
38%
Warren
7%

Butler
13%

Dearborn
4%
Clermont
9%

Brown
3%

Ohio
0%
Gallatin
2%
Grant
3%
