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1 of
3
Dan River Steam Station CSA Supplement 2
Ta
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1 ‐1:
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Total Depth ft btocProgram
GW
A
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D
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C
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GW
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C
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GW
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1
7
C
A
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A
GW
A
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9
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C
A
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GW
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D
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9
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1
.
5
5
3
6
.
5
5
4
1
.
9
5
C
A
M
A
GW
A
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S
S
h
a
l
l
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w
9
9
8
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9
6
7
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2
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1
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1
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3
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9
4
5
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4
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4
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5
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2
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0
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5
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5
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5
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5
5
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A
M
A
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A
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D
D
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p
9
9
9
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3
9
0
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6
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7
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1
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9
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9
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6
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6
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0
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3
2
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2
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4
2
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2
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4
2
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4
6
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A
M
A
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A
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D
D
e
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p
1
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0
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5
2
6
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8
8
1
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9
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7
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5
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3
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5
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0
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4
0
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1
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4
5
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1
5
5
2
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6
5
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A
M
A
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A
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D
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1
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0
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5
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3
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A
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2
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7
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5
6
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7
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8
6
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A
M
A
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A
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D
D
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9
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6
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9
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1
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9
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9
3
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A
M
A
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A
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S
S
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9
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2
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0
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8
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3
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6
1
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A
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A
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D
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1
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0
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4
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6
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9
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6
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8
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9
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6
3
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9
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1
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2
9
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A
M
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A
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S
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1
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0
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9
2
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1
6
1
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8
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7
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5
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2
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6
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2
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0
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1
8
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6
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3
3
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6
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3
3
.
9
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C
A
M
A
GW
A
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D
e
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p
9
9
9
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7
2
2
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0
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1
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5
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3
7
5
7
4
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0
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2
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5
6
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6
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0
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3
6
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5
6
4
1
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5
6
4
1
.
8
6
C
A
M
A
GW
A
‐3S
S
h
a
l
l
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w
9
9
9
,
7
2
8
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3
3
1
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7
9
0
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3
2
6
.
7
0
5
7
3
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9
8
2
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5
7
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2
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0
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1
6
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3
7
2
6
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3
7
2
6
.
6
7
C
A
M
A
GW
A
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D
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9
9
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1
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8
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3
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1
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1
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1
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4
1
C
A
M
A
GW
A
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S
h
a
l
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9
9
9
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1
7
5
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1
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3
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5
7
5
2
7
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8
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3
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2
2
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2
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0
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2
3
.
2
2
3
8
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2
2
3
8
.
5
2
C
A
M
A
GW
A
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R
B
e
d
r
o
c
k
9
9
8
,
9
8
0
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5
7
1
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7
9
0
,
9
8
7
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7
9
4
9
9
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7
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2
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6
2
P
V
C
6
.
0
0
5
7
.
6
2
6
2
.
6
2
6
2
.
9
2
C
A
M
A
GW
A
‐5B
R
D
B
e
d
r
o
c
k
9
9
8
,
9
7
6
.
8
2
1
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7
9
0
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9
7
5
.
6
7
5
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2
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1
4
2
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5
4
P
V
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5
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0
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1
2
1
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5
4
1
3
1
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5
4
1
3
3
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0
4
C
A
M
A
GW
A
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D
e
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p
9
9
6
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6
8
8
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5
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1
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7
8
8
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7
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2
5
5
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2
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7
5
P
V
C
6
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0
0
2
8
.
2
5
3
3
.
2
5
3
3
.
5
5
C
A
M
A
GW
A
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S
h
a
l
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w
9
9
6
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6
9
1
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5
8
1
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7
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2
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7
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4
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3
8
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2
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0
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8
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6
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6
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9
2
C
A
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A
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D
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9
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6
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0
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7
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0
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A
M
A
GW
A
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S
h
a
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9
9
7
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7
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4
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8
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1
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2
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2
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0
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3
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8
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7
9
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9
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9
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A
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A
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D
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p
9
9
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2
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5
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7
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6
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0
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7
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1
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2
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1
8
4
2
.
4
8
C
A
M
A
GW
A
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S
h
a
l
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w
9
9
9
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2
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5
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7
8
1
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4
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2
.
0
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8
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3
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3
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3
7
2
3
.
6
7
C
A
M
A
GW
A
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D
e
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p
9
9
9
,
8
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7
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7
9
1
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7
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8
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1
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3
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3
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6
1
1
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3
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2
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8
9
P
V
C
6
.
0
0
6
9
.
8
9
7
4
.
8
9
7
5
.
1
9
C
A
M
A
GW
A
‐9S
S
h
a
l
l
o
w
9
9
9
,
8
9
2
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1
3
1
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7
8
8
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1
7
0
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7
6
6
1
1
.
7
2
2
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8
5
P
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2
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0
0
3
4
.
8
5
4
9
.
8
5
5
0
.
1
5
C
A
M
A
MW
‐22
B
R
B
e
d
r
o
c
k
9
9
6
,
9
2
4
.
8
7
1
,
7
8
9
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2
8
1
.
9
6
5
0
2
.
3
2
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2
9
P
V
C
6
.
0
0
5
7
.
7
1
6
2
.
7
1
6
3
.
0
1
C
A
M
A
MW
‐23
B
R
B
e
d
r
o
c
k
9
9
9
,
3
3
4
.
8
9
1
,
7
8
6
,
3
6
2
.
5
9
5
2
7
.
5
5
3
.
0
9
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V
C
6
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0
0
5
9
.
0
9
6
4
.
0
9
6
4
.
3
9
C
A
M
A
MW
‐30
1
B
R
B
e
d
r
o
c
k
1
,
0
0
0
,
0
8
5
.
2
1
1
,
7
8
9
,
7
2
4
.
7
6
5
9
3
.
5
5
3
.
2
1
P
V
C
6
.
0
0
4
0
.
2
1
4
5
.
2
1
4
5
.
5
1
C
A
M
A
Pa
g
e
2 of
3
Dan River Steam Station CSA Supplement 2
Ta
b
l
e
1 ‐1:
We
l
l
Co
n
s
t
r
u
c
t
i
o
n
In
f
o
r
m
a
t
i
o
n
Mo
n
i
t
o
r
i
n
g
We
l
l
ID
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Mo
n
i
t
o
r
i
n
g
We
l
l
Ty
p
e
‐
No
r
t
h
i
n
g
ft
Ea
s
t
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g
ft
TO
C
El
e
v
a
t
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o
n
ft
bt
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c
Ca
s
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g
St
i
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k
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ft
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s
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g
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e
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in
To
p
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e
n
ft
bt
o
c
Bo
t
t
o
m
of
Sc
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e
n
ft
bt
o
c
Total Depth ft btocProgram
MW
‐30
3
B
R
B
e
d
r
o
c
k
9
9
9
,
8
2
7
.
7
9
1
,
7
8
9
,
6
6
9
.
9
9
6
5
1
.
3
7
3
.
0
1
P
V
C
6
.
0
0
1
4
0
.
0
1
1
4
5
.
0
1
1
4
5
.
3
1
C
A
M
A
MW
‐30
6
B
R
B
e
d
r
o
c
k
9
9
9
,
3
7
6
.
3
5
1
,
7
8
9
,
6
3
1
.
2
2
6
1
3
.
6
2
2
.
1
6
P
V
C
6
.
0
0
1
0
4
.
1
6
1
0
9
.
1
6
1
0
9
.
4
6
C
A
M
A
MW
‐30
8
B
R
B
e
d
r
o
c
k
9
9
8
,
6
4
9
.
5
1
1
,
7
8
9
,
6
8
9
.
6
1
5
3
2
.
5
9
2
.
1
3
P
V
C
6
.
0
0
7
9
.
1
3
8
4
.
1
3
8
4
.
4
3
C
A
M
A
MW
‐31
0
B
R
B
e
d
r
o
c
k
9
9
8
,
3
5
0
.
6
6
1
,
7
8
9
,
3
9
5
.
7
2
5
3
8
.
9
1
‐0.
2
1
P
V
C
6
.
0
0
7
2
.
7
9
7
7
.
7
9
7
8
.
0
9
C
A
M
A
MW
‐31
1
B
R
B
e
d
r
o
c
k
9
9
7
,
7
1
5
.
0
7
1
,
7
8
9
,
9
2
2
.
0
8
5
3
7
.
7
3
1
.
5
2
P
V
C
6
.
0
0
1
2
1
.
5
2
1
2
6
.
5
2
1
2
6
.
8
2
C
A
M
A
MW
‐31
4
B
R
B
e
d
r
o
c
k
9
9
7
,
6
4
5
.
7
8
1
,
7
8
9
,
0
6
9
.
2
6
5
3
9
.
7
5
‐0.
3
1
P
V
C
6
.
0
0
6
8
.
6
9
7
3
.
6
9
7
3
.
9
9
C
A
M
A
MW
‐31
5
B
R
B
e
d
r
o
c
k
9
9
8
,
7
0
7
.
1
3
1
,
7
8
9
,
0
8
0
.
4
5
5
7
0
.
7
5
3
.
2
3
P
V
C
6
.
0
0
6
2
.
9
3
7
7
.
9
3
7
8
.
2
3
C
A
M
A
MW
‐31
7
B
R
B
e
d
r
o
c
k
9
9
9
,
1
2
2
.
8
7
1
,
7
8
8
,
3
1
5
.
5
1
5
7
1
.
9
3
2
.
1
9
P
V
C
6
.
0
0
8
5
.
1
9
9
0
.
1
9
9
0
.
4
9
C
A
M
A
MW
‐31
7
B
R
L
B
e
d
r
o
c
k
9
9
9
,
0
5
7
.
5
9
1
,
7
8
8
,
3
5
6
.
7
1
5
7
1
.
2
0
2
.
8
1
P
V
C
5
.
0
0
1
8
1
.
8
1
1
9
1
.
8
1
1
9
2
.
6
1
C
A
M
A
MW
‐31
8
D
D
e
e
p
9
9
9
,
0
6
6
.
8
1
1
,
7
8
9
,
1
2
7
.
5
2
5
6
7
.
2
1
2
.
6
2
P
V
C
6
.
0
0
4
7
.
1
2
5
2
.
1
2
6
2
.
4
2
C
A
M
A
MW
‐20
D
D
e
e
p
1
,
0
0
0
,
6
9
2
.
0
0
1
,
7
8
8
,
9
2
3
.
0
0
5
6
2
.
2
3
2
.
8
1
P
V
C
2
.
0
0
2
.
8
1
2
.
8
1
5
6
2
.
2
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:
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3 of
3
Dan River Steam Station CSA Supplement 2
Ta
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1 ‐2:
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1 of
18
Dan River Steam Station CSA Supplement 2
Ta
b
l
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1 ‐2:
Hi
s
t
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r
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c
a
l
Da
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a
fr
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l
l
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6
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Pa
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2 of
18
Dan River Steam Station CSA Supplement 2
Ta
b
l
e
1 ‐2:
Hi
s
t
o
r
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c
a
l
Da
t
a
fr
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m
NP
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p
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We
l
l
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NC
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C
2L
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p
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4 of
18
Dan River Steam Station CSA Supplement 2
Ta
b
l
e
1 ‐2:
Hi
s
t
o
r
i
c
a
l
Da
t
a
fr
o
m
NP
D
E
S
Co
m
p
l
i
a
n
c
e
an
d
Vo
l
u
n
t
a
r
y
We
l
l
s
NC
A
C
2L
St
a
n
d
a
r
d
:
N
S
N
S
N
S
N
S
6
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5
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8.
5
5
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0
1
0
2
5
0
Un
i
t
s
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µ
Ω /c
m
m
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L
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U
m
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/
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m
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m
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2
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0
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0
Pa
g
e
5 of
18
Dan River Steam Station CSA Supplement 2
Ta
b
l
e
1 ‐2:
Hi
s
t
o
r
i
c
a
l
Da
t
a
fr
o
m
NP
D
E
S
Co
m
p
l
i
a
n
c
e
an
d
Vo
l
u
n
t
a
r
y
We
l
l
s
NC
A
C
2L
St
a
n
d
a
r
d
:
N
S
N
S
N
S
N
S
6
.
5
‐
8.
5
5
0
0
1
0
2
5
0
Un
i
t
s
:
°
C
m
V
µ
Ω /c
m
m
g
/
L
S
U
m
g
/
L
m
g
/
L
m
g
/
L
We
l
l
ID
S
a
m
p
l
e
Da
t
e
T
e
m
p
e
r
a
t
u
r
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O
R
P
S
p
e
c
i
f
i
c
Co
n
d
u
c
t
i
v
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t
y
D
O
p
H
(F
i
e
l
d
)
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N
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C
h
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s
:
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10
.
In
t
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r
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m
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x
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u
m
Al
l
o
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(I
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s
)
ca
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be
fo
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n
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in
Ap
p
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n
d
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x
#1
of
15
A
NC
A
C
Su
b
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h
a
p
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r
02
L
Cl
a
s
s
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f
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c
a
t
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s
and Water Quality Standards
Ap
p
l
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c
a
b
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to
th
e
Gr
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n
d
w
a
t
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s
of
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SU
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me
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va
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me
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St
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Ap
p
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b
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to the Groundwaters of
No
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St
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d
s
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r
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of
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2
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me
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Pa
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6 of
18
Dan River Steam Station CSA Supplement 2
Ta
b
l
e
1 ‐2:
Hi
s
t
o
r
i
c
a
l
Da
t
a
fr
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m
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p
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We
l
l
s
NC
A
C
2L
St
a
n
d
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r
d
:
Un
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s
:
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7 of
18
Dan River Steam Station CSA Supplement 2
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10
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18
Dan River Steam Station CSA Supplement 2
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g
e
11
of
18
Dan River Steam Station CSA Supplement 2
Ta
b
l
e
1 ‐2:
Hi
s
t
o
r
i
c
a
l
Da
t
a
fr
o
m
NP
D
E
S
Co
m
p
l
i
a
n
c
e
an
d
Vo
l
u
n
t
a
r
y
We
l
l
s
NC
A
C
2L
St
a
n
d
a
r
d
:
Un
i
t
s
:
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l
l
ID
S
a
m
p
l
e
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t
e
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5
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2
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5
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5
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No
t
e
s
:
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h
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L
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St
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l
i
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a
Pa
g
e
12
of
18
Dan River Steam Station CSA Supplement 2
Ta
b
l
e
1 ‐2:
Hi
s
t
o
r
i
c
a
l
Da
t
a
fr
o
m
NP
D
E
S
Co
m
p
l
i
a
n
c
e
an
d
Vo
l
u
n
t
a
r
y
We
l
l
s
NC
A
C
2L
St
a
n
d
a
r
d
:
Un
i
t
s
:
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l
l
ID
S
a
m
p
l
e
Da
t
e
MW
‐9
1
1
/
2
9
/
1
9
9
3
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‐9
4
/
4
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1
9
9
4
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5
/
2
3
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1
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9
4
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8
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1
9
9
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13
of
18
Dan River Steam Station CSA Supplement 2
Ta
b
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1 ‐2:
Hi
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t
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Da
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fr
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NC
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14
of
18
Dan River Steam Station CSA Supplement 2
Ta
b
l
e
1 ‐2:
Hi
s
t
o
r
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c
a
l
Da
t
a
fr
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m
NP
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Co
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Pa
g
e
15
of
18
Dan River Steam Station CSA Supplement 2
Ta
b
l
e
1 ‐2:
Hi
s
t
o
r
i
c
a
l
Da
t
a
fr
o
m
NP
D
E
S
Co
m
p
l
i
a
n
c
e
an
d
Vo
l
u
n
t
a
r
y
We
l
l
s
NC
A
C
2L
St
a
n
d
a
r
d
:
Un
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t
s
:
We
l
l
ID
S
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Dan River Steam Station CSA Supplement 2
Ta
b
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1 ‐2:
Hi
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NC
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2L
St
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17
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18
Dan River Steam Station CSA Supplement 2
Ta
b
l
e
1 ‐2:
Hi
s
t
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r
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c
a
l
Da
t
a
fr
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m
NP
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p
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l
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s
NC
A
C
2L
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n
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d
:
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t
s
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l
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p
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No
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s
:
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10
.
In
t
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x
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Al
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o
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r
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s
(I
M
A
C
s
)
ca
n
be
fo
u
n
d
in
Ap
p
e
n
d
i
x
#1
of
15
A
NC
A
C
Su
b
c
h
a
p
t
e
r
02
L
Cl
a
s
s
i
f
i
c
a
t
i
o
n
s
and Water Quality Standards
Ap
p
l
i
c
a
b
l
e
to
th
e
Gr
o
u
n
d
w
a
t
e
r
s
of
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r
t
h
Ca
r
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i
n
a
SU
in
d
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c
a
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s
pH
va
l
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s
me
a
s
u
r
e
d
in
st
a
n
d
a
r
d
un
i
t
s
NT
U
in
d
i
c
a
t
e
s
tu
r
b
i
d
i
t
y
va
l
u
e
s
me
a
s
u
r
e
d
in
Ne
p
h
a
l
o
m
e
t
r
i
c
Tu
r
b
i
d
i
t
y
Un
i
t
s
Pa
r
a
m
e
t
e
r
s
ar
e
co
m
p
a
r
e
d
to
st
a
n
d
a
r
d
s
fo
u
n
d
in
15
A
NC
A
C
Su
b
c
h
a
p
t
e
r
02
L
Cl
a
s
s
i
f
i
c
a
t
i
o
n
s
an
d
Wa
t
e
r
Qu
a
l
i
t
y
St
a
n
d
a
r
d
s
Ap
p
l
i
c
a
b
l
e
to the Groundwaters of
No
r
t
h
Ca
r
o
l
i
n
a
2L
St
a
n
d
a
r
d
s
ar
e
es
t
a
b
l
i
s
h
e
d
as
pa
r
t
of
15
A
NC
A
C
02
L
.0
2
0
2
°C
in
d
i
c
a
t
e
s
te
m
p
e
r
a
t
u
r
e
me
a
s
u
r
e
d
in
de
g
r
e
e
s
ce
l
s
i
u
s
mV
in
d
i
c
a
t
e
s
ox
i
d
a
t
i
o
n
/
r
e
d
u
c
t
i
o
n
po
t
e
n
t
i
a
l
me
a
s
u
r
e
d
in
mi
l
l
i
v
o
l
t
s
µΩ /c
m
in
d
i
c
a
t
e
s
sp
e
c
i
f
i
c
co
n
d
u
c
t
i
v
i
t
y
me
a
s
u
r
e
d
in
mi
c
r
o
m
h
o
s
pe
r
ce
n
t
i
m
e
t
e
r
mg
/
L
in
d
i
c
a
t
e
s
co
n
c
e
n
t
r
a
t
i
o
n
s
me
a
s
u
r
e
d
in
mi
l
l
i
g
r
a
m
s
pe
r
li
t
e
r
µg
/
L
in
d
i
c
a
t
e
s
co
n
c
e
n
t
r
a
t
i
o
n
s
me
a
s
u
r
e
d
in
mi
c
r
o
g
r
a
m
s
pe
r
li
t
e
r
Pa
g
e
18
of
18
Dan River Steam Station CSA Supplement 2
Ta
b
l
e
1 ‐3:
2L
Gr
o
u
n
d
w
a
t
e
r
St
a
n
d
a
r
d
Ex
c
e
e
d
a
n
c
e
s
fr
o
m
NP
D
E
S
Sa
m
p
l
i
n
g
2L
St
a
n
d
a
r
d
:
1
1
0
7
0
0
3
0
0
5
0
2
5
0
,
0
0
0
5
0
0
,
0
0
0
0
.
2
6
.
5
– 8.5
Un
i
t
s
:
µ
g
/
L
µ
g
/
L
µ
g
/
L
µ
g
/
L
µ
g
/
L
µ
g
/
L
µ
g
/
L
µ
g
/
L
S
U
We
l
l
ID
D
a
t
e
Ra
n
g
e
A
n
t
i
m
o
n
y
A
r
s
e
n
i
c
B
o
r
o
n
I
r
o
n
M
a
n
g
a
n
e
s
e
S
u
l
f
a
t
e
T
D
S
T
h
a
l
l
i
u
m
p
H
MW
‐20
S
1
/
4
/
2
0
1
1
– 5/
2
/
2
0
1
6
1
.
0
4
N
o
Ex
c
e
e
d
a
n
c
e
s
N
o
Ex
c
e
e
d
a
n
c
e
s
2
,
3
5
0
– 3,
1
9
0
7
8
9
– 94
5
N
o
Ex
c
e
e
d
a
n
c
e
s
N
o
Ex
c
e
e
d
a
n
c
e
s
0
.
4
5
5
.
8
2
– 6.24
MW
‐20
D
1
/
4
/
2
0
1
1
– 5/
2
/
2
0
1
6
1
.
0
6
– 1.
1
N
o
Ex
c
e
e
d
a
n
c
e
s
N
o
Ex
c
e
e
d
a
n
c
e
s
N
o
Ex
c
e
e
d
a
n
c
e
s
4
8
9
– 55
3
N
o
Ex
c
e
e
d
a
n
c
e
s
N
o
Ex
c
e
e
d
a
n
c
e
s
N
o
Exceedances
N
o
Exceedances
MW
‐21
S
1
/
4
/
2
0
1
1
– 5/
2
/
2
0
1
6
1
.
0
2
– 1.
3
3
1
6
.
8
– 44
.
7
N
o
Ex
c
e
e
d
a
n
c
e
s
N
o
Ex
c
e
e
d
a
n
c
e
s
3
0
6
– 1,
5
3
0
N
o
Ex
c
e
e
d
a
n
c
e
s
N
o
Ex
c
e
e
d
a
n
c
e
s
N
o
Exceedances
6
.
4
5
– 6.47
MW
‐21
D
1
/
4
/
2
0
1
1
– 5/
2
/
2
0
1
6
1
.
0
5
N
o
Ex
c
e
e
d
a
n
c
e
s
N
o
Ex
c
e
e
d
a
n
c
e
s
3
7
6
– 70
1
8
2
0
– 1,
0
7
0
2
7
0
,
0
0
0
– 35
0
,
0
0
0
6
0
0
,
0
0
0
– 77
0
,
0
0
0
N
o
Exceedances
N
o
Exceedances
MW
‐22
S
1
/
1
2
/
2
0
1
2
– 5/
2
/
2
0
1
6
1
.
7
2
N
o
Ex
c
e
e
d
a
n
c
e
s
8
2
9
– 90
3
7
,
2
5
0
– 19
,
4
0
0
5
5
9
– 96
5
N
o
Ex
c
e
e
d
a
n
c
e
s
N
o
Ex
c
e
e
d
a
n
c
e
s
N
o
Exceedances
N
o
Exceedances
MW
‐22
D
1
/
1
2
/
2
0
1
2
– 5/
2
/
2
0
1
6
1
.
0
6
– 1.
9
3
N
o
Ex
c
e
e
d
a
n
c
e
s
7
1
1
– 80
6
3
4
2
– 1,
0
1
0
5
4
– 26
1
N
o
Ex
c
e
e
d
a
n
c
e
s
N
o
Ex
c
e
e
d
a
n
c
e
s
N
o
Exceedances
N
o
Exceedances
MW
‐23
D
1
/
4
/
2
0
1
1
– 5/
2
/
2
0
1
6
1
.
0
4
– 1.
4
N
o
Ex
c
e
e
d
a
n
c
e
s
N
o
Ex
c
e
e
d
a
n
c
e
s
3
2
6
– 1,
7
0
0
6
1
– 56
6
N
o
Ex
c
e
e
d
a
n
c
e
s
N
o
Ex
c
e
e
d
a
n
c
e
s
N
o
Exceedances
5
.
6
7
– 6.49
No
t
e
s
:
1.2.3.4.5.
mg
/
L
in
d
i
c
a
t
e
s
co
n
c
e
n
t
r
a
t
i
o
n
s
me
a
s
u
r
e
d
in
mi
l
l
i
g
r
a
m
s
pe
r
li
t
e
r
Qu
a
l
i
t
y
St
a
n
d
a
r
d
s
Ap
p
l
i
c
a
b
l
e
to
th
e
Gr
o
u
n
d
w
a
t
e
r
s
of
No
r
t
h
Ca
r
o
l
i
n
a
µg
/
L
in
d
i
c
a
t
e
s
co
n
c
e
n
t
r
a
t
i
o
n
s
me
a
s
u
r
e
d
in
mi
c
r
o
g
r
a
m
s
pe
r
li
t
e
r
SU
in
d
i
c
a
t
e
s
pH
va
l
u
e
s
me
a
s
u
r
e
d
in
st
a
n
d
a
r
d
un
i
t
s
Pa
r
a
m
e
t
e
r
s
ar
e
co
m
p
a
r
e
d
to
st
a
n
d
a
r
d
s
fo
u
n
d
in
15
A
NC
A
C
Su
b
c
h
a
p
t
e
r
02
L
Cl
a
s
s
i
f
i
c
a
t
i
o
n
s
an
d
Wa
t
e
r
Qu
a
l
i
t
y
St
a
n
d
a
r
d
s
Ap
p
l
i
c
a
b
l
e
to
th
e
Gr
o
u
n
d
w
a
t
e
r
s
of
No
r
t
h
Ca
r
o
l
i
n
a
2L
St
a
n
d
a
r
d
s
ar
e
es
t
a
b
l
i
s
h
e
d
as
pa
r
t
of
15
A
NC
A
C
02
L
.0
2
0
2
In
t
e
r
i
m
Ma
x
i
m
u
m
Al
l
o
w
a
b
l
e
Co
n
c
e
n
t
r
a
t
i
o
n
s
(I
M
A
C
s
)
ca
n
be
fo
u
n
d
in
Ap
p
e
n
d
i
x
#1
of
15
A
NC
A
C
Su
b
c
h
a
p
t
e
r
02
L
Cl
a
s
s
i
f
i
c
a
t
i
o
n
s
an
d
Wa
t
e
r
Pa
g
e
1 of
1
Dan River Steam Station CSA Supplement 2
Ta
b
l
e
2 ‐1:
Re
s
p
o
n
s
e
s
to
Gl
o
b
a
l
NC
D
E
Q
Co
m
m
e
n
t
s
Ty
p
e
Co
m
m
e
n
t
Nu
m
b
e
r
Co
m
m
e
n
t
G
e
n
e
r
a
l
Re
s
o
l
u
t
i
o
n
Ge
n
e
r
a
l
1
Ch
e
c
k
la
t
i
t
u
d
e
an
d
lo
n
g
i
t
u
d
e
sh
o
w
n
on
re
p
o
r
t
co
v
e
r
pa
g
e
s
(t
h
e
co
n
v
e
r
s
i
o
n
ap
p
e
a
r
s
to
be
in
c
o
r
r
e
c
t
on
th
e
Mo
o
r
e
s
v
i
l
l
e
re
g
i
o
n
re
p
o
r
t
s
an
d
ne
e
d
s
to
be
re
c
o
n
c
i
l
e
d
)
.
HD
R
wi
l
l
re
v
i
e
w
an
d
pr
o
v
i
d
e
co
r
r
e
c
t
e
d
la
t
i
t
u
d
e
an
d
lo
n
g
i
t
u
d
e
co
o
r
d
i
n
a
t
e
s
for the sites in forthcoming
re
p
o
r
t
s
,
if
ne
e
d
e
d
.
Ba
c
k
g
r
o
u
n
d
2
Us
e
te
r
m
i
n
o
l
o
g
y
PE
P
A
“p
r
o
v
i
s
i
o
n
a
l
es
t
i
m
a
t
e
s
fo
r
pu
r
p
o
s
e
s
of
as
s
e
s
s
m
e
n
t
”
pr
o
v
i
d
e
fo
r
ba
c
k
g
r
o
u
n
d
co
n
c
e
n
t
r
a
t
i
o
n
s
of
CO
I
s
.
"P
r
o
p
o
s
e
d
Pr
o
v
i
s
i
o
n
a
l
Ba
c
k
g
r
o
u
n
d
Co
n
c
e
n
t
r
a
t
i
o
n
s
"
or
PP
B
C
s
is
th
e
terminology used for statistically
de
t
e
r
m
i
n
e
d
ba
c
k
g
r
o
u
n
d
co
n
c
e
n
t
r
a
t
i
o
n
s
in
th
e
CA
P
re
p
o
r
t
i
n
g
.
PP
B
C
s
are discussed in CAP Part 1, Section 2.
Th
e
ap
p
r
o
a
c
h
to
re
f
i
n
e
PP
B
C
s
wh
e
n
ad
d
i
t
i
o
n
a
l
da
t
a
is
av
a
i
l
a
b
l
e
is
pr
e
s
e
n
t
e
d
in CSA Supplement 2, Section
4.
CO
I
3
Us
e
re
s
u
l
t
s
fr
o
m
po
r
e
w
a
t
e
r
,
gr
o
u
n
d
w
a
t
e
r
an
d
ot
h
e
r
me
d
i
a
to
de
v
e
l
o
p
CO
I
li
s
t
.
CO
I
s
we
r
e
se
l
e
c
t
e
d
ba
s
e
d
on
ex
c
e
e
d
a
n
c
e
s
fo
u
n
d
in
po
r
e
w
a
t
e
r
,
gr
o
u
n
d
w
a
t
e
r
,
soil, and surface water
sa
m
p
l
e
re
s
u
l
t
s
.
CO
I
4
Cr
(
V
I
)
– in
c
l
u
d
e
as
CO
I
at
ea
c
h
si
t
e
du
e
to
in
t
e
r
e
s
t
an
d
du
e
to
re
c
e
p
t
o
r
we
l
l
re
s
u
l
t
s
.
Us
e
NC
D
H
H
S
sc
r
e
e
n
i
n
g
va
l
u
e
.
He
x
a
v
a
l
e
n
t
Ch
r
o
m
i
u
m
is
in
c
l
u
d
e
d
as
a CO
I
in
CA
P
Pa
r
t
1 da
t
a
ta
b
l
e
s
and is considered with respect to the
NC
DH
H
S
sc
r
e
e
n
i
n
g
le
v
e
l
an
d
ha
s
be
e
n
ca
r
r
i
e
d
fo
r
w
a
r
d
wi
t
h
su
b
s
e
q
u
e
n
t
evaluations. Samples were
an
a
l
y
z
e
d
fo
r
He
x
a
v
a
l
e
n
t
Ch
r
o
m
i
u
m
in
se
l
e
c
t
gr
o
u
n
d
w
a
t
e
r
mo
n
i
t
o
r
i
n
g
wells, and further Cr(VI) evaluation
ma
y
ta
k
e
pl
a
c
e
ba
s
e
d
on
th
e
re
s
u
l
t
s
of
ea
c
h
si
t
e
re
s
p
e
c
t
i
v
e
l
y
.
CA
P
Part 1, Section 1.9.2 states that Cr(VI) is
in
c
l
u
d
e
d
in
th
e
CO
I
li
s
t
.
CO
I
5
Ne
e
d
to
ev
a
l
u
a
t
e
va
n
a
d
i
u
m
an
d
st
r
o
n
t
i
u
m
at
ev
e
r
y
si
t
e
to
sh
o
w
di
f
f
e
r
e
n
c
e
s
be
t
w
e
e
n
ba
c
k
g
r
o
u
n
d
co
n
c
e
n
t
r
a
t
i
o
n
s
an
d
po
t
e
n
t
i
a
l
so
u
r
c
e
‐re
l
a
t
e
d
co
n
c
e
n
t
r
a
t
i
o
n
s
.
Va
n
a
d
i
u
m
ha
s
be
e
n
co
n
s
i
d
e
r
e
d
ac
r
o
s
s
th
e
si
t
e
s
in
CS
A
re
p
o
r
t
i
n
g
.
St
r
o
n
t
i
u
m
was not included in the CSA
ta
b
l
e
s
,
ho
w
e
v
e
r
st
r
o
n
t
i
u
m
da
t
a
wa
s
co
l
l
e
c
t
e
d
wi
t
h
ot
h
e
r
co
n
s
t
i
t
u
e
n
t
s
,
including vanadium, and is
pr
e
s
e
n
t
e
d
in
th
e
CS
A
Su
p
p
l
e
m
e
n
t
2.
CO
I
-
R
e
c
e
p
t
o
r
s
6
A
d
d
ev
a
l
u
a
t
i
o
n
of
re
c
e
p
t
o
r
we
l
l
s
in
CA
P
.
Wa
t
e
r
su
p
p
l
y
we
l
l
s
ar
e
sh
o
w
n
on
Fi
g
u
r
e
1 ‐3 in
th
e
CS
A
Su
p
p
l
e
m
e
n
t
2 along with analytical results
fa
c
i
l
i
t
a
t
i
n
g
th
e
in
t
e
r
p
r
e
t
a
t
i
o
n
of
re
c
e
p
t
o
r
wa
t
e
r
qu
a
l
i
t
y
re
l
a
t
i
v
e
to
si
t
e
water quality.
CO
I
-
R
e
c
e
p
t
o
r
s
7
Pr
i
v
a
t
e
an
d
pu
b
l
i
c
wa
t
e
r
su
p
p
l
y
we
l
l
s
sa
m
p
l
e
d
sh
o
u
l
d
be
sh
o
w
n
on
a ma
p
wi
t
h
zo
o
m
in
bo
x
e
s
sh
o
w
i
n
g
co
n
c
e
n
t
r
a
t
i
o
n
re
s
u
l
t
s
ev
e
n
if
be
l
o
w
2L
.
Wa
t
e
r
su
p
p
l
y
we
l
l
s
ar
e
sh
o
w
n
on
Fi
g
u
r
e
1 ‐3 in
th
e
CS
A
Su
p
p
l
e
m
e
n
t
2 along with analytical results
fa
c
i
l
i
t
a
t
i
n
g
th
e
in
t
e
r
p
r
e
t
a
t
i
o
n
of
re
c
e
p
t
o
r
wa
t
e
r
qu
a
l
i
t
y
re
l
a
t
i
v
e
to
si
t
e
water quality.
CO
I
-
R
e
c
e
p
t
o
r
s
8
A
d
d
ta
b
l
e
wi
t
h
al
l
re
c
e
p
t
o
r
we
l
l
re
s
u
l
t
s
.
Wa
t
e
r
su
p
p
l
y
we
l
l
s
ar
e
sh
o
w
n
on
Fi
g
u
r
e
1 ‐3 in
th
e
CS
A
Su
p
p
l
e
m
e
n
t
2 along with analytical results
fa
c
i
l
i
t
a
t
i
n
g
th
e
in
t
e
r
p
r
e
t
a
t
i
o
n
of
re
c
e
p
t
o
r
wa
t
e
r
qu
a
l
i
t
y
re
l
a
t
i
v
e
to
si
t
e
water quality.
CO
I
-
R
e
c
e
p
t
o
r
s
9
Al
l
pr
i
v
a
t
e
re
c
e
p
t
o
r
we
l
l
s
sh
o
w
n
on
fi
g
u
r
e
s
(u
s
e
or
ad
d
DE
Q
de
s
i
g
n
a
t
i
o
n
s
)
.
Sh
o
w
re
s
u
l
t
s
fo
r
de
t
e
c
t
i
o
n
co
n
s
t
i
t
u
e
n
t
s
.
Ad
d
st
r
o
n
t
i
u
m
.
Al
l
wa
t
e
r
su
p
p
l
y
we
l
l
s
ar
e
sh
o
w
n
on
Fi
g
u
r
e
1 ‐3.
Th
o
s
e
wa
t
e
r
su
p
p
l
y
wells that can be shown in the
vi
e
w
p
o
r
t
s
of
th
e
th
e
po
t
e
n
t
i
o
m
e
t
r
i
c
su
r
f
a
c
e
an
d
is
o
c
o
n
c
e
n
t
r
a
t
i
o
n
fi
g
u
r
e
s
in the CSA Supplement 2 are also
in
c
l
u
d
e
d
.
A ta
b
l
e
of
an
a
l
y
t
i
c
a
l
re
s
u
l
t
s
,
in
c
l
u
d
i
n
g
st
r
o
n
t
i
u
m
,
is
in
c
l
u
d
e
d
on Figure 1 ‐3.
CO
I
10
Ad
d
to
t
a
l
ur
a
n
i
u
m
an
d
Ra
2
2
6
+
2
2
8
.
DE
Q
co
n
s
i
d
e
r
s
ra
d
i
o
n
u
c
l
i
d
e
s
to
be
a dr
i
v
e
r
of
al
p
h
a
ac
t
i
v
i
t
y
in
th
e
as
h
ba
s
i
n
s
.
Sa
m
p
l
e
th
e
fo
l
l
o
w
i
n
g
lo
c
a
t
i
o
n
s
bo
t
h
be
l
o
w
as
h
po
n
d
s
an
d
ot
h
e
r
do
w
n
g
r
a
d
i
e
n
t
ar
e
a
s
wh
e
r
e
ot
h
e
r
co
n
s
t
i
t
u
e
n
t
co
n
c
e
n
t
r
a
t
i
o
n
s
ar
e
hi
g
h
:
Do
w
n
g
r
a
d
i
e
n
t
mo
n
i
t
o
r
i
n
g
we
l
l
lo
c
a
t
i
o
n
s
,
at
lo
c
a
t
i
o
n
s
wi
t
h
ex
c
e
e
d
a
n
c
e
s
,
an
d
at
ba
c
k
g
r
o
u
n
d
lo
c
a
t
i
o
n
s
.
Ur
a
n
i
u
m
an
d
Ra
2
2
6
+
2
2
8
ma
y
be
in
c
l
u
d
e
d
in
NP
D
E
S
mo
n
i
t
o
r
i
n
g
.
Li
s
t
Fe
d
e
r
a
l
MC
L
as
st
a
n
d
a
r
d
fo
r
Ra
22
6
‐22
8
an
d
ur
a
n
i
u
m
.
Se
l
e
c
t
we
l
l
s
lo
c
a
t
e
d
do
w
n
s
t
r
e
a
m
an
d
al
o
n
g
tr
a
n
s
e
c
t
s
we
r
e
sa
m
p
l
e
d
for these constituents in the CSA and
Po
s
t
‐CS
A
sa
m
p
l
i
n
g
pe
r
i
o
d
s
.
At
th
e
ti
m
e
of
th
e
CS
A
Su
p
p
l
e
m
e
n
t
2,
th
e
analytical results from Round 5 had
be
e
n
re
c
e
i
v
e
d
an
d
up
o
n
re
v
i
e
w
,
we
r
e
re
c
o
m
m
e
n
d
e
d
fo
r
re
‐is
s
u
e
pr
i
o
r
to completing review and inclusion
in
th
e
CS
A
Su
p
p
l
e
m
e
n
t
2.
Up
o
n
re
c
e
i
p
t
,
th
e
s
e
da
t
a
wi
l
l
be
pr
o
v
i
d
e
d
in a subsequent submittal.
So
u
r
c
e
C
h
a
r
a
c
t
e
r
i
z
a
t
i
o
n
11
Ad
d
r
e
s
s
so
i
l
s
as
be
i
n
g
pr
i
m
a
r
y
an
d
se
c
o
n
d
a
r
y
so
u
r
c
e
s
– ad
d
r
e
s
s
in
CA
P
an
d
CS
A
su
p
p
l
e
m
e
n
t
.
A se
p
a
r
a
t
e
ri
s
k
as
s
e
s
s
m
e
n
t
ha
s
be
e
n
pr
o
v
i
d
e
d
su
b
s
e
q
u
e
n
t
to
th
e
CS
A
report by Duke Energy via Haley &
Al
d
r
i
t
c
h
.
So
u
r
c
e
C
h
a
r
a
c
t
e
r
i
z
a
t
i
o
n
12
De
s
c
r
i
b
e
ho
w
ge
o
c
h
e
m
i
c
a
l
co
n
d
i
t
i
o
n
s
ma
y
af
f
e
c
t
re
l
e
a
s
e
of
na
t
u
r
a
l
l
y
oc
c
u
r
r
i
n
g
co
n
s
t
i
t
u
e
n
t
s
su
c
h
as
ir
o
n
an
d
ma
n
g
a
n
e
s
e
.
Di
s
c
u
s
s
i
o
n
of
ge
o
c
h
e
m
i
c
a
l
co
n
d
i
t
i
o
n
s
we
r
e
pr
o
v
i
d
e
d
in
CA
P
Pa
r
t
2 with geochemical modeling results.
So
u
r
c
e
C
h
a
r
a
c
t
e
r
i
z
a
t
i
o
n
13
So
i
l
to
be
id
e
n
t
i
f
i
e
d
as
se
c
o
n
d
a
r
y
so
u
r
c
e
– du
e
to
le
a
c
h
i
n
g
of
as
h
on
t
o
un
s
a
t
u
r
a
t
e
d
so
i
l
.
A se
p
a
r
a
t
e
ri
s
k
as
s
e
s
s
m
e
n
t
ha
s
be
e
n
pr
o
v
i
d
e
d
su
b
s
e
q
u
e
n
t
to
th
e
CS
A
report by Duke Energy via Haley &
Al
d
r
i
t
c
h
.
Pa
g
e
1 of
7
Dan River Steam Station CSA Supplement 2
Ta
b
l
e
2 ‐1:
Re
s
p
o
n
s
e
s
to
Gl
o
b
a
l
NC
D
E
Q
Co
m
m
e
n
t
s
Ty
p
e
Co
m
m
e
n
t
Nu
m
b
e
r
Co
m
m
e
n
t
G
e
n
e
r
a
l
Re
s
o
l
u
t
i
o
n
Ba
c
k
g
r
o
u
n
d
14
Ba
c
k
g
r
o
u
n
d
so
i
l
co
n
c
e
n
t
r
a
t
i
o
n
s
ne
e
d
to
be
ev
a
l
u
a
t
e
d
.
Na
t
i
v
e
so
i
l
s
ma
y
be
a so
u
r
c
e
ba
s
e
d
on
ge
o
c
h
e
m
i
c
a
l
co
n
d
i
t
i
o
n
s
in
/
b
e
n
e
a
t
h
th
e
as
h
po
n
d
s
.
Ne
e
d
to
ad
d
r
e
s
s
ba
c
k
g
r
o
u
n
d
so
i
l
co
n
d
i
t
i
o
n
s
an
d
re
l
a
t
i
o
n
s
h
i
p
to
ob
s
e
r
v
e
d
2L
ex
c
e
e
d
a
n
c
e
s
.
Pr
o
p
o
s
e
d
Pr
o
v
i
s
i
o
n
a
l
Ba
c
k
g
r
o
u
n
d
Co
n
c
e
n
t
r
a
t
i
o
n
s
or
PP
B
C
s
ar
e
di
s
c
u
s
s
e
d
in CAP Part 1, Section 2. The
ap
p
r
o
a
c
h
to
re
f
i
n
e
PP
B
C
s
wh
e
n
ad
d
i
t
i
o
n
a
l
da
t
a
is
av
a
i
l
a
b
l
e
is
pr
e
s
e
n
t
e
d
in CSA Supplement 2, Section 4.
Ba
c
k
g
r
o
u
n
d
15
Pr
o
v
i
d
e
“p
r
o
v
i
s
i
o
n
a
l
es
t
i
m
a
t
e
s
”
of
ba
c
k
g
r
o
u
n
d
if
th
e
r
e
ar
e
in
s
u
f
f
i
c
i
e
n
t
nu
m
b
e
r
s
of
sa
m
p
l
e
s
fo
r
st
a
t
i
s
t
i
c
s
.
"P
r
o
p
o
s
e
d
Pr
o
v
i
s
i
o
n
a
l
Ba
c
k
g
r
o
u
n
d
Co
n
c
e
n
t
r
a
t
i
o
n
s
"
or
PP
B
C
s
is
th
e
terminology used for statistically
de
t
e
r
m
i
n
e
d
ba
c
k
g
r
o
u
n
d
co
n
c
e
n
t
r
a
t
i
o
n
s
in
th
e
CA
P
re
p
o
r
t
i
n
g
.
PP
B
C
s
are discussed in CAP Part 1, Section 2.
Th
e
ap
p
r
o
a
c
h
to
re
f
i
n
e
PP
B
C
s
wh
e
n
ad
d
i
t
i
o
n
a
l
da
t
a
is
av
a
i
l
a
b
l
e
is
pr
e
s
e
n
t
e
d
in CSA Supplement 2, Section
4.
Ba
c
k
g
r
o
u
n
d
16
A si
m
i
l
a
r
an
a
l
y
s
i
s
/
e
v
a
l
u
a
t
i
o
n
of
do
w
n
g
r
a
d
i
e
n
t
so
i
l
s
an
d
th
e
i
r
re
l
a
t
i
o
n
s
h
i
p
to
2L
ex
c
e
e
d
a
n
c
e
s
al
s
o
ne
e
d
s
to
be
in
c
l
u
d
e
d
in
th
e
CA
P
.
Pr
o
p
o
s
e
d
Pr
o
v
i
s
i
o
n
a
l
Ba
c
k
g
r
o
u
n
d
Co
n
c
e
n
t
r
a
t
i
o
n
s
or
PP
B
C
s
ar
e
di
s
c
u
s
s
e
d
in CAP Part 1, Section 2. The
ap
p
r
o
a
c
h
to
re
f
i
n
e
PP
B
C
s
wh
e
n
ad
d
i
t
i
o
n
a
l
da
t
a
is
av
a
i
l
a
b
l
e
is
pr
e
s
e
n
t
e
d
in CSA Supplement 2, Section 4.
Ba
c
k
g
r
o
u
n
d
17
Po
t
e
n
t
i
a
l
re
l
e
a
s
e
me
c
h
a
n
i
s
m
s
ne
e
d
to
be
co
n
s
i
d
e
r
e
d
in
th
e
CA
P
(i
.
e
.
,
mi
g
r
a
t
i
o
n
of
le
a
c
h
a
t
e
be
n
e
a
t
h
th
e
as
h
ba
s
i
n
,
et
c
.
)
.
Di
s
c
u
s
s
i
o
n
of
po
t
e
n
t
i
a
l
mi
g
r
a
t
i
o
n
pa
t
h
w
a
y
s
is
di
s
c
u
s
s
e
d
in
CA
P
Pa
r
t
2, Section 3.3
Ba
c
k
g
r
o
u
n
d
18
Ba
c
k
g
r
o
u
n
d
de
t
e
r
m
i
n
a
t
i
o
n
s
.
Ba
c
k
g
r
o
u
n
d
co
n
c
e
n
t
r
a
t
i
o
n
s
ne
e
d
to
be
ev
a
l
u
a
t
e
d
to
de
t
e
r
m
i
n
e
si
t
e
‐sp
e
c
i
f
i
c
co
n
s
t
i
t
u
e
n
t
co
n
c
e
n
t
r
a
t
i
o
n
le
v
e
l
s
an
d
th
i
s
ev
a
l
u
a
t
i
o
n
ne
e
d
s
to
be
in
c
l
u
d
e
d
in
CA
P
.
Us
e
al
l
av
a
i
l
a
b
l
e
hi
s
t
o
r
i
c
da
t
a
fr
o
m
co
m
p
l
i
a
n
c
e
we
l
l
s
an
d
ne
w
l
y
in
s
t
a
l
l
e
d
we
l
l
s
.
"P
r
o
p
o
s
e
d
Pr
o
v
i
s
i
o
n
a
l
Ba
c
k
g
r
o
u
n
d
Co
n
c
e
n
t
r
a
t
i
o
n
s
"
or
PP
B
C
s
is
th
e
terminology used for statistically
de
t
e
r
m
i
n
e
d
ba
c
k
g
r
o
u
n
d
co
n
c
e
n
t
r
a
t
i
o
n
s
in
th
e
CA
P
re
p
o
r
t
i
n
g
.
PP
B
C
s
are discussed in CAP Part 1, Section 2.
Th
e
ap
p
r
o
a
c
h
to
re
f
i
n
e
PP
B
C
s
wh
e
n
ad
d
i
t
i
o
n
a
l
da
t
a
is
av
a
i
l
a
b
l
e
is
pr
e
s
e
n
t
e
d
in CSA Supplement 2, Section
4.
Ba
c
k
g
r
o
u
n
d
19
Ba
c
k
g
r
o
u
n
d
gr
o
u
n
d
w
a
t
e
r
mo
n
i
t
o
r
i
n
g
we
l
l
s
ne
e
d
to
be
sa
m
p
l
e
d
2
mo
r
e
ti
m
e
s
be
f
o
r
e
th
e
en
d
of
20
1
5
(s
a
m
p
l
e
s
ne
e
d
to
be
sp
e
c
i
a
t
e
d
)
.
Th
e
s
e
sa
m
p
l
e
s
ha
v
e
be
e
n
co
l
l
e
c
t
e
d
.
Da
t
a
fr
o
m
Ro
u
n
d
s
2 th
r
o
u
g
h
4 was included in the CAP Part 2.
Ba
c
k
g
r
o
u
n
d
20
Se
p
a
r
a
t
e
ba
c
k
g
r
o
u
n
d
co
n
c
e
n
t
r
a
t
i
o
n
s
ne
e
d
to
be
de
t
e
r
m
i
n
e
d
fo
r
sh
a
l
l
o
w
,
in
t
e
r
m
e
d
i
a
t
e
an
d
de
e
p
fl
o
w
la
y
e
r
s
(a
s
we
l
l
as
an
y
ot
h
e
r
si
t
e
‐sp
e
c
i
f
i
c
co
n
d
i
t
i
o
n
s
li
k
e
we
t
l
a
n
d
s
)
.
"P
r
o
p
o
s
e
d
Pr
o
v
i
s
i
o
n
a
l
Ba
c
k
g
r
o
u
n
d
Co
n
c
e
n
t
r
a
t
i
o
n
s
"
or
PP
B
C
s
ar
e
di
s
c
u
s
s
e
d
in CAP Part 1, Section 2. The
ap
p
r
o
a
c
h
to
re
f
i
n
e
PP
B
C
s
wh
e
n
ad
d
i
t
i
o
n
a
l
da
t
a
is
av
a
i
l
a
b
l
e
is
pr
e
s
e
n
t
e
d
in CSA Supplement 2, Section 4.
Th
i
s
ap
p
r
o
a
c
h
in
c
l
u
d
e
s
co
n
s
i
d
e
r
a
t
i
o
n
to
th
e
s
e
ca
l
c
u
a
t
i
o
n
s
by
fl
o
w
la
y
e
r
.
Ba
c
k
g
r
o
u
n
d
21
Us
e
al
l
av
a
i
l
a
b
l
e
si
t
e
da
t
a
(i
n
c
l
u
d
e
ex
a
m
p
l
e
ba
c
k
g
r
o
u
n
d
we
l
l
s
PH
R
,
FG
D
,
Cr
a
i
g
Rd
.
)
.
Ba
c
k
g
r
o
u
n
d
da
t
a
fr
o
m
hi
s
t
o
r
i
c
a
l
so
u
r
c
e
s
wa
s
ut
i
l
i
z
e
d
wh
e
r
e
ap
p
l
i
c
a
b
l
e
in the CAP Part 2.
We
l
l
a
n
d
C
o
n
s
t
i
t
u
e
n
t
s
22
We
l
l
s
mu
s
t
me
e
t
2C
ru
l
e
re
q
u
i
r
e
m
e
n
t
s
;
tu
r
b
i
d
i
t
y
ca
n
n
o
t
im
p
a
c
t
re
s
u
l
t
s
.
Re
s
u
l
t
s
fr
o
m
Ro
u
n
d
5 sa
m
p
l
i
n
g
ar
e
pr
e
s
e
n
t
e
d
in
th
e
CS
A
Su
p
p
l
e
m
e
n
t
2 and wells with turbidity results
ab
o
v
e
10
NT
U
ar
e
id
e
n
t
i
f
i
e
d
so
th
a
t
re
s
u
l
t
s
ma
y
be
qu
a
l
i
f
i
e
d
up
o
n
re
v
i
e
w
.
We
l
l
a
n
d
C
o
n
s
t
i
t
u
e
n
t
s
23
El
e
v
a
t
e
d
pH
an
d
tu
r
b
i
d
i
t
y
mu
s
t
be
ad
d
r
e
s
s
e
d
or
we
l
l
mu
s
t
be
re
d
e
v
e
l
o
p
e
d
or
re
p
l
a
c
e
d
.
Du
k
e
En
e
r
g
y
ha
s
in
s
t
a
l
l
e
d
ad
d
i
t
i
o
n
a
l
mo
n
i
t
o
r
i
n
g
we
l
l
s
to
ad
d
r
e
s
s
co
n
c
e
r
n
s
with elevated pH and turbidity
se
e
n
wh
e
n
sa
m
p
l
i
n
g
as
we
l
l
as
to
re
f
i
n
e
un
d
e
r
s
t
a
n
d
i
n
g
of
ex
c
e
e
d
a
n
c
e
s
.
Results from the Round 5,
in
c
l
u
d
i
n
g
ad
d
i
t
i
o
n
a
l
as
s
e
s
s
m
e
n
t
we
l
l
s
,
ha
s
be
e
n
in
c
l
u
d
e
d
in
CS
A
Su
p
p
l
e
m
e
n
t
2.
We
l
l
a
n
d
C
o
n
s
t
i
t
u
e
n
t
s
24
In
c
l
u
d
e
di
s
c
u
s
s
i
o
n
of
pH
an
d
tu
r
b
i
d
i
t
y
in
ba
c
k
g
r
o
u
n
d
we
l
l
di
s
c
u
s
s
i
o
n
.
"P
r
o
p
o
s
e
d
Pr
o
v
i
s
i
o
n
a
l
Ba
c
k
g
r
o
u
n
d
Co
n
c
e
n
t
r
a
t
i
o
n
s
"
or
PP
B
C
s
ar
e
di
s
c
u
s
s
e
d
in CAP Part 1, Section 2. The
ap
p
r
o
a
c
h
to
re
f
i
n
e
PP
B
C
s
wh
e
n
ad
d
i
t
i
o
n
a
l
da
t
a
is
av
a
i
l
a
b
l
e
is
pr
e
s
e
n
t
e
d
in CSA Supplement 2, Section 4.
Th
i
s
ap
p
r
o
a
c
h
in
c
l
u
d
e
s
co
n
s
i
d
e
r
a
t
i
o
n
to
th
e
s
e
ca
l
c
u
a
t
i
o
n
s
by
ut
i
l
i
z
i
n
g
viable samples below 10 NTU.
We
l
l
a
n
d
C
o
n
s
t
i
t
u
e
n
t
s
25
R
e
s
u
l
t
s
ab
o
v
e
10
NT
U
to
be
re
m
o
v
e
d
fr
o
m
da
t
a
se
t
fo
r
st
a
t
i
s
t
i
c
s
.
"P
r
o
p
o
s
e
d
Pr
o
v
i
s
i
o
n
a
l
Ba
c
k
g
r
o
u
n
d
Co
n
c
e
n
t
r
a
t
i
o
n
s
"
or
PP
B
C
s
ar
e
di
s
c
u
s
s
e
d
in CAP Part 1, Section 2. The
ap
p
r
o
a
c
h
to
re
f
i
n
e
PP
B
C
s
wh
e
n
ad
d
i
t
i
o
n
a
l
da
t
a
is
av
a
i
l
a
b
l
e
is
pr
e
s
e
n
t
e
d
in CSA Supplement 2, Section 4.
Th
i
s
ap
p
r
o
a
c
h
in
c
l
u
d
e
s
co
n
s
i
d
e
r
a
t
i
o
n
to
th
e
s
e
ca
l
c
u
a
t
i
o
n
s
by
ut
i
l
i
z
i
n
g
viable samples below 10 NTU.
So
i
l
C
o
n
t
a
m
i
n
a
t
i
o
n
26
So
i
l
co
n
t
a
m
i
n
a
t
i
o
n
pl
u
m
e
s
do
no
t
ap
p
e
a
r
to
be
we
l
l
de
l
i
n
e
a
t
e
d
.
Sh
o
w
ex
t
e
n
t
of
pl
a
n
fi
g
u
r
e
s
an
d
on
cr
o
s
s
se
c
t
i
o
n
s
.
Ve
r
t
i
c
a
l
de
l
i
n
e
a
t
i
o
n
of
CO
I
s
ar
e
no
t
e
d
on
cr
o
s
s
se
c
t
i
o
n
s
in
c
l
u
d
e
d
in
the CSA Supplement 2.
Pa
g
e
2 of
7
Dan River Steam Station CSA Supplement 2
Ta
b
l
e
2 ‐1:
Re
s
p
o
n
s
e
s
to
Gl
o
b
a
l
NC
D
E
Q
Co
m
m
e
n
t
s
Ty
p
e
Co
m
m
e
n
t
Nu
m
b
e
r
Co
m
m
e
n
t
G
e
n
e
r
a
l
Re
s
o
l
u
t
i
o
n
So
i
l
C
o
n
t
a
m
i
n
a
t
i
o
n
27
Co
m
p
a
r
e
so
i
l
re
s
u
l
t
s
to
Pr
e
l
i
m
i
n
a
r
y
So
i
l
Re
m
e
d
i
a
t
i
o
n
Go
a
l
s
(P
S
R
G
)
fo
r
pr
o
t
e
c
t
i
o
n
of
gr
o
u
n
d
w
a
t
e
r
st
a
n
d
a
r
d
s
(P
O
G
)
.
Wh
e
r
e
ad
d
i
t
i
o
n
a
l
so
i
l
sa
m
p
l
e
s
we
r
e
co
l
l
e
c
t
e
d
as
pa
r
t
of
th
e
in
s
t
a
l
l
a
t
i
o
n
of additional assessment wells,
th
o
s
e
re
s
u
l
t
s
wi
l
l
be
pr
e
s
e
n
t
e
d
to
PS
R
G
PO
G
st
a
n
d
a
r
d
s
.
So
i
l
C
o
n
t
a
m
i
n
a
t
i
o
n
28
MR
L
vs
.
PO
G
ar
e
is
s
u
e
fo
r
se
l
e
c
t
e
d
co
n
s
t
i
t
u
e
n
t
s
;
th
i
s
ma
y
re
q
u
i
r
e
re
s
a
m
p
l
i
n
g
.
Du
k
e
En
e
r
g
y
wo
r
k
e
d
wi
t
h
th
e
la
b
s
to
re
d
u
c
e
th
e
re
p
o
r
t
i
n
g
li
m
i
t
s
.
Ho
w
e
v
e
r
,
lowering the MRL to below the
PO
G
wa
s
no
t
ab
l
e
to
be
ac
h
i
e
v
e
d
to
da
t
e
fo
r
ce
r
t
a
i
n
co
n
s
t
i
t
u
e
n
t
s
.
So
i
l
C
o
n
t
a
m
i
n
a
t
i
o
n
29
So
i
l
s
PS
R
G
s
,
de
t
e
c
t
i
o
n
li
m
i
t
s
ab
o
v
e
st
a
n
d
a
r
d
s
is
pr
o
b
l
e
m
a
t
i
c
.
Re
v
i
e
w
IH
S
B
Gu
i
d
e
l
i
n
e
s
fo
r
As
s
e
s
s
m
e
n
t
an
d
Cl
e
a
n
u
p
se
c
t
i
o
n
4.
1
.
1
.
2
to
de
v
e
l
o
p
si
t
e
sp
e
c
i
f
i
c
ba
c
k
g
r
o
u
n
d
va
l
u
e
s
fo
r
so
i
l
,
if
ap
p
l
i
c
a
b
l
e
Du
k
e
En
e
r
g
y
wo
r
k
e
d
wi
t
h
th
e
la
b
s
to
re
d
u
c
e
th
e
re
p
o
r
t
i
n
g
li
m
i
t
s
.
Ho
w
e
v
e
r
,
lowering the MRL to below the
PO
G
wa
s
no
t
ab
l
e
to
be
ac
h
i
e
v
e
d
to
da
t
e
fo
r
ce
r
t
a
i
n
co
n
s
t
i
t
u
e
n
t
s
.
So
i
l
C
o
n
t
a
m
i
n
a
t
i
o
n
30
C
r
(
V
I
)
is
dr
i
v
i
n
g
ri
s
k
,
us
e
Cr
(
V
I
)
in
re
v
i
e
w
.
I
n
th
e
CA
P
re
p
o
r
t
i
n
g
as
we
l
l
as
CS
A
Su
p
p
l
e
m
e
n
t
2,
Cr
(
V
I
)
is
ad
d
e
d
to
the list of COIs in groundwater.
So
i
l
C
o
n
t
a
m
i
n
a
t
i
o
n
31
N
e
e
d
to
co
m
p
a
r
e
so
i
l
s
re
s
u
l
t
s
to
Cr
(
V
I
)
(n
o
t
Cr
(
I
I
I
)
)
.
So
i
l
s
wi
l
l
be
co
m
p
a
r
e
d
to
th
e
PS
R
G
PO
G
Cr
(
V
I
)
st
a
n
d
a
r
d
of
3.
8
mg
/
k
g
in subsequent reporting, where
ad
d
i
t
i
o
n
a
l
so
i
l
sa
m
p
l
e
s
we
r
e
co
l
l
e
c
t
e
d
.
Hy
d
r
o
l
o
g
y
/
G
e
o
l
o
g
y
a
n
d
Ch
e
m
i
c
a
l
C
o
n
t
r
o
l
s
32
Hy
d
r
o
l
o
g
y
/
g
e
o
l
o
g
i
c
co
n
t
r
o
l
s
an
d
th
e
ef
f
e
c
t
s
on
co
n
t
a
m
i
n
a
n
t
di
s
t
r
i
b
u
t
i
o
n
an
d
tr
a
n
s
p
o
r
t
ar
e
no
t
di
s
c
u
s
s
e
d
in
CS
A
.
Di
s
c
u
s
s
re
l
a
t
i
v
e
to
DO
,
pH
,
Eh
,
et
c
.
It
is
im
p
e
r
a
t
i
v
e
th
a
t
th
i
s
di
s
c
u
s
s
i
o
n
be
in
c
l
u
d
e
d
as
pa
r
t
of
CA
P
#1
as
th
i
s
is
re
q
u
i
r
e
m
e
n
t
of
CA
M
A
.
Th
e
di
s
c
u
s
s
i
o
n
ca
n
be
re
f
i
n
e
d
in
CA
P
#2
.
On
Ju
n
e
25
,
20
1
5
,
NC
D
E
Q
re
q
u
e
s
t
e
d
th
a
t
th
e
s
e
ge
o
c
h
e
m
i
c
a
l
is
s
u
e
s
be addressed in a Site Conceptual
Mo
d
e
l
.
Th
i
s
to
p
i
c
wa
s
in
t
r
o
d
u
c
e
d
in
th
e
CS
A
an
d
an
n
o
u
n
c
e
d
th
a
t
th
e
SCM would be refined as an iterative
pr
o
c
e
s
s
in
th
e
fo
r
t
h
c
o
m
i
n
g
CA
P
.
CA
P
Pa
r
t
1 Se
c
t
i
o
n
3.
2
.
2
in
c
l
u
d
e
d
discussion of general geochemical
ch
a
r
a
c
t
e
r
i
s
t
i
c
s
su
c
h
as
ca
t
i
o
n
s
/
a
n
i
o
n
s
,
re
d
o
x
po
t
e
n
t
i
a
l
,
so
l
u
t
e
sp
e
c
i
a
t
i
o
n
,
and Kd testing. These items were
fu
r
t
h
e
r
ad
d
r
e
s
s
e
d
in
CA
P
Pa
r
t
2 Se
c
t
i
o
n
2.
4
.
4
,
an
d
Se
c
t
i
o
n
3.
3
.
Hy
d
r
o
l
o
g
y
/
G
e
o
l
o
g
y
a
n
d
Ch
e
m
i
c
a
l
C
o
n
t
r
o
l
s
33
Di
s
c
u
s
s
ho
w
ge
o
c
h
e
m
i
c
a
l
co
n
d
i
t
i
o
n
s
af
f
e
c
t
co
n
t
a
m
i
n
a
n
t
di
s
t
r
i
b
u
t
i
o
n
?
(G
e
o
c
h
e
m
i
c
a
l
“h
a
l
o
”
re
l
e
a
s
i
n
g
Mn
an
d
Fe
)
.
On
Ju
n
e
25
,
20
1
5
,
NC
D
E
Q
re
q
u
e
s
t
e
d
th
a
t
th
e
s
e
ge
o
c
h
e
m
i
c
a
l
is
s
u
e
s
be addressed in a Site Conceptual
Mo
d
e
l
.
Th
i
s
to
p
i
c
wa
s
in
t
r
o
d
u
c
e
d
in
th
e
CS
A
an
d
an
n
o
u
n
c
e
d
th
a
t
th
e
SCM would be refined as an iterative
pr
o
c
e
s
s
in
th
e
fo
r
t
h
c
o
m
i
n
g
CA
P
.
CA
P
Pa
r
t
1 Se
c
t
i
o
n
3.
2
.
2
in
c
l
u
d
e
d
discussion of general geochemical
ch
a
r
a
c
t
e
r
i
s
t
i
c
s
su
c
h
as
ca
t
i
o
n
s
/
a
n
i
o
n
s
,
re
d
o
x
po
t
e
n
t
i
a
l
,
so
l
u
t
e
sp
e
c
i
a
t
i
o
n
,
and Kd testing. These items are
fu
r
t
h
e
r
ad
d
r
e
s
s
e
d
in
CA
P
Pa
r
t
2 Se
c
t
i
o
n
2.
4
.
4
:
Si
t
e
Ge
o
c
h
e
m
i
s
t
r
y
an
d
Influence on COIs, which treats spatial
di
s
t
r
i
b
u
t
i
o
n
of
gr
o
u
n
d
w
a
t
e
r
ge
o
c
h
e
m
i
s
t
r
y
re
l
a
t
i
v
e
to
th
e
so
u
r
c
e
ar
e
a
.
Hy
d
r
o
l
o
g
y
/
G
e
o
l
o
g
y
a
n
d
Ch
e
m
i
c
a
l
C
o
n
t
r
o
l
s
34
S
p
e
c
i
f
y
wh
e
r
e
di
f
f
e
r
e
n
c
e
s
ex
i
s
t
fr
o
m
Le
G
r
a
n
d
co
n
c
e
p
t
u
a
l
mo
d
e
l
.
Th
e
CA
P
Pa
r
t
2 re
p
o
r
t
st
a
t
e
s
wh
e
r
e
th
e
mo
d
e
l
is
co
n
s
i
s
t
e
n
t
wi
t
h
Le
G
r
a
n
d
,
specifically in the Groundwater
Mi
g
r
a
t
i
o
n
su
b
s
e
c
t
i
o
n
,
an
d
th
e
CO
I
Oc
c
u
r
r
e
n
c
e
an
d
Di
s
t
r
i
b
u
t
i
o
n
Se
c
t
i
o
n
.
Hy
d
r
o
l
o
g
y
/
G
e
o
l
o
g
y
a
n
d
Ch
e
m
i
c
a
l
C
o
n
t
r
o
l
s
35
Gr
o
u
n
d
w
a
t
e
r
ve
l
o
c
i
t
i
e
s
in
be
d
r
o
c
k
an
d
tr
a
n
s
i
t
i
o
n
zo
n
e
ap
p
e
a
r
to
be
to
o
hi
g
h
.
Ve
r
i
f
y
or
co
r
r
e
c
t
th
e
s
e
va
l
u
e
s
.
De
s
c
r
i
b
e
tr
a
n
s
m
i
s
s
i
v
i
t
y
co
n
c
e
p
t
ve
r
s
u
s
jo
i
n
t
fl
o
w
ve
l
o
c
i
t
y
.
Th
e
s
e
va
l
u
e
s
we
r
e
co
r
r
e
c
t
e
d
an
d
up
d
a
t
e
d
in
CA
P
Pa
r
t
2 Ap
p
e
n
d
i
x
A.
Hy
d
r
o
l
o
g
y
/
G
e
o
l
o
g
y
a
n
d
Ch
e
m
i
c
a
l
C
o
n
t
r
o
l
s
36
E
x
p
l
a
i
n
wh
y
on
e
co
n
t
a
m
i
n
a
n
t
ma
y
be
el
e
v
a
t
e
d
in
a pa
r
t
i
c
u
l
a
r
ar
e
a
.
CA
P
Pa
r
t
2 Se
c
t
i
o
n
3.
7
in
c
l
u
d
e
d
an
ex
p
a
n
d
e
d
di
s
c
u
s
s
i
o
n
of
si
t
e
ge
o
c
h
e
m
i
c
a
l
controls on contaminant
mo
b
i
l
i
t
y
an
d
mi
g
r
a
t
i
o
n
to
ad
d
r
e
s
s
th
i
s
co
n
c
e
r
n
.
Hy
d
r
o
l
o
g
y
/
G
e
o
l
o
g
y
a
n
d
Ch
e
m
i
c
a
l
C
o
n
t
r
o
l
s
37
D
e
s
c
r
i
b
e
ho
w
co
n
s
t
i
t
u
e
n
t
s
ar
e
mo
b
i
l
i
z
e
d
or
at
t
e
n
u
a
t
e
d
.
CA
P
Pa
r
t
2 Se
c
t
i
o
n
3.
7
in
c
l
u
d
e
d
an
ex
p
a
n
d
e
d
di
s
c
u
s
s
i
o
n
of
si
t
e
ge
o
c
h
e
m
i
c
a
l
controls on contaminant
mo
b
i
l
i
t
y
an
d
mi
g
r
a
t
i
o
n
to
ad
d
r
e
s
s
th
i
s
co
n
c
e
r
n
.
Hy
d
r
o
l
o
g
y
/
G
e
o
l
o
g
y
a
n
d
Ch
e
m
i
c
a
l
C
o
n
t
r
o
l
s
38
De
s
c
r
i
b
e
ge
o
c
h
e
m
i
c
a
l
co
n
d
i
t
i
o
n
s
an
d
me
c
h
a
n
i
s
m
s
,
an
d
ch
a
r
g
e
s
,
al
o
n
g
fl
o
w
pa
t
h
s
.
DE
Q
co
n
s
i
d
e
r
s
fl
o
w
pa
t
h
s
to
be
fr
o
m
th
e
ma
x
i
m
u
m
co
n
c
e
n
t
r
a
t
i
o
n
fo
r
a CO
I
to
a re
c
e
p
t
o
r
or
to
th
e
co
m
p
l
i
a
n
c
e
bo
u
n
d
a
r
y
.
Th
e
gr
o
u
n
d
w
a
t
e
r
mo
d
e
l
co
n
s
i
d
e
r
s
li
n
e
a
r
ad
s
o
r
p
t
i
o
n
(F
r
e
u
n
d
l
i
c
h
ad
s
o
r
p
t
i
o
n
for select COIs in the Buck
mo
d
e
l
)
fo
r
CO
I
s
(e
x
c
e
p
t
su
l
f
a
t
e
an
d
ch
l
o
r
i
d
e
)
.
Th
e
ad
s
o
r
p
t
i
o
n
te
r
m
(Kd) is uniform within the model
do
m
a
i
n
,
in
c
l
u
d
i
n
g
fr
o
m
th
e
ac
t
i
v
e
an
d
in
a
c
t
i
v
e
as
h
ba
s
i
n
s
/
s
t
o
r
a
g
e
(s
o
u
r
c
e
s
)
to downgradient monitor wells
an
d
th
e
co
m
p
l
i
a
n
c
e
bo
u
n
d
a
r
y
.
CA
P
Pa
r
t
2,
Ap
p
e
n
d
i
x
B,
gr
o
u
n
d
w
a
t
e
r
model.
Hy
d
r
o
l
o
g
y
/
G
e
o
l
o
g
y
a
n
d
Ch
e
m
i
c
a
l
C
o
n
t
r
o
l
s
39
De
s
c
r
i
b
e
na
t
u
r
e
of
so
r
p
t
i
v
e
ma
t
e
r
i
a
l
s
pr
e
s
e
n
t
in
th
r
e
e
‐pa
r
t
sy
s
t
e
m
an
d
al
o
n
g
fl
o
w
pa
t
h
s
to
re
c
e
p
t
o
r
s
.
So
r
p
t
i
o
n
co
n
s
t
a
n
t
s
an
d
ca
l
c
u
l
a
t
i
o
n
s
ar
e
de
s
c
r
i
b
e
d
in
CA
P
Pa
r
t
2 Se
c
t
i
o
n
4.3, in the methodology subsection
Pa
g
e
3 of
7
Dan River Steam Station CSA Supplement 2
Ta
b
l
e
2 ‐1:
Re
s
p
o
n
s
e
s
to
Gl
o
b
a
l
NC
D
E
Q
Co
m
m
e
n
t
s
Ty
p
e
Co
m
m
e
n
t
Nu
m
b
e
r
Co
m
m
e
n
t
G
e
n
e
r
a
l
Re
s
o
l
u
t
i
o
n
Hy
d
r
o
l
o
g
y
/
G
e
o
l
o
g
y
a
n
d
Ch
e
m
i
c
a
l
C
o
n
t
r
o
l
s
40
De
s
c
r
i
b
e
ho
w
bo
r
o
n
,
su
l
f
a
t
e
,
TD
S
“i
s
l
a
n
d
s
”
ar
e
lo
c
a
t
e
d
al
o
n
g
fl
o
w
pa
t
h
s
an
d
ho
w
th
e
s
e
ar
e
co
n
s
i
d
e
r
e
d
/
i
n
c
o
r
p
o
r
a
t
e
d
in
t
o
HG
C
M
an
d
nu
m
e
r
i
c
a
l
mo
d
e
l
s
.
Th
e
gr
o
u
n
d
w
a
t
e
r
mo
d
e
l
is
se
t
u
p
pe
r
so
u
r
c
e
ar
e
a
an
d
th
e
n
ca
l
i
b
r
a
t
e
d
to concentrations observed in
do
w
n
g
r
a
d
i
e
n
t
mo
n
i
t
o
r
we
l
l
s
.
Ca
l
i
b
r
a
t
i
o
n
to
ob
s
e
r
v
e
d
co
n
c
e
n
t
r
a
t
i
o
n
s
is achieved by adjusting source
co
n
c
e
n
t
r
a
t
i
o
n
s
wi
t
h
i
n
ac
t
i
v
e
/
i
n
a
c
t
i
v
e
as
h
ba
s
i
n
s
an
d
as
h
st
o
r
a
g
e
ar
e
a
s
within the measured values,
ad
j
u
s
t
i
n
g
hy
d
r
a
u
l
i
c
co
n
d
u
c
t
i
v
i
t
y
ba
s
e
d
on
re
p
o
r
t
e
d
va
l
u
e
s
,
ad
j
u
s
t
i
n
g
kd based on lab data, and other
me
a
s
u
r
e
d
hy
d
r
o
g
e
o
l
o
g
i
c
pr
o
p
e
r
t
i
e
s
.
Th
e
ca
l
i
b
r
a
t
i
o
n
at
t
e
m
p
t
s
to
ma
t
c
h
concentrations observed in
do
w
n
g
r
a
d
i
e
n
t
mo
n
i
t
o
r
we
l
l
s
by
ma
t
c
h
i
n
g
th
e
fl
o
w
pa
t
h
s
an
d
th
u
s
th
e
observed COI “islands”. The model
di
d
no
t
in
c
o
r
p
o
r
a
t
e
TD
S
(b
o
r
o
n
an
d
su
l
f
a
t
e
ar
e
bo
t
h
in
c
l
u
d
e
d
in
th
e
groundwater model. CAP Part 2,
Ap
p
e
n
d
i
x
B,
gr
o
u
n
d
w
a
t
e
r
mo
d
e
l
.
Hy
d
r
o
l
o
g
y
/
G
e
o
l
o
g
y
a
n
d
Ch
e
m
i
c
a
l
C
o
n
t
r
o
l
s
41
Su
b
s
u
r
f
a
c
e
dr
a
i
n
a
g
e
sy
s
t
e
m
s
at
di
k
e
/
d
a
m
s
sh
o
u
l
d
be
sh
o
w
n
an
d
po
t
e
n
t
i
a
l
im
p
a
c
t
s
to
fa
t
e
& tr
a
n
s
p
o
r
t
mo
d
e
l
i
n
g
sh
o
u
l
d
be
de
s
c
r
i
b
e
d
in
in
hy
d
r
o
g
e
o
l
o
g
i
c
an
d
ge
o
c
h
e
m
i
c
a
l
co
n
c
e
p
t
u
a
l
mo
d
e
l
s
.
Su
b
s
u
r
f
a
c
e
dr
a
i
n
a
g
e
sy
s
t
e
m
s
ar
e
sh
o
w
n
an
d
di
s
c
u
s
s
e
d
in
Se
c
t
i
o
n
4 of the CSA reports. They are shown in
th
e
CS
A
Se
c
t
i
o
n
4 Fi
g
u
r
e
s
.
Hy
d
r
o
l
o
g
y
/
G
e
o
l
o
g
y
a
n
d
Ch
e
m
i
c
a
l
C
o
n
t
r
o
l
s
42
S
h
o
w
me
a
s
u
r
e
d
wa
t
e
r
le
v
e
l
s
on
po
n
d
s
,
st
r
e
a
m
s
,
ri
v
e
r
s
.
Po
n
d
,
ri
v
e
r
,
an
d
la
k
e
el
e
v
a
t
i
o
n
s
wi
l
l
be
sh
o
w
n
on
fi
g
u
r
e
s
wh
e
r
e
ap
p
l
i
c
a
b
l
e
.
For example, in the CSA
Su
p
p
l
e
m
e
n
t
2,
th
e
s
e
el
e
v
a
t
i
o
n
s
ar
e
in
c
l
u
d
e
d
on
th
e
sh
a
l
l
o
w
po
t
e
n
t
i
o
m
e
t
r
i
c
figures, but not on all flow
la
y
e
r
s
.
Hy
d
r
o
g
e
o
l
o
g
i
c
a
n
d
O
t
h
e
r
Ge
o
c
h
e
m
i
c
a
l
C
o
n
c
e
p
t
u
a
l
Mo
d
e
l
s
43
R
e
f
i
n
e
d
co
n
c
e
p
t
u
a
l
mo
d
e
l
ne
e
d
s
to
be
pr
e
s
e
n
t
e
d
in
CA
P
I.
S
i
t
e
Co
n
c
e
p
t
u
a
l
Mo
d
e
l
s
we
r
e
up
d
a
t
e
d
an
d
in
c
l
u
d
e
d
in
th
e
CA
P
Pa
r
t
2.
Hy
d
r
o
g
e
o
l
o
g
i
c
a
n
d
O
t
h
e
r
Ge
o
c
h
e
m
i
c
a
l
C
o
n
c
e
p
t
u
a
l
Mo
d
e
l
s
44
Hy
d
r
o
g
e
o
an
d
ge
o
c
h
e
m
i
c
a
l
co
n
c
e
p
t
u
a
l
mo
d
e
l
s
ne
e
d
to
be
di
s
c
u
s
s
e
d
in
te
r
m
s
of
sp
e
c
i
f
i
c
so
u
r
c
e
ar
e
a
s
.
In
c
l
u
d
e
up
g
r
a
d
i
e
n
t
,
so
u
r
c
e
,
an
d
do
w
n
g
r
a
d
i
e
n
t
.
De
v
e
l
o
p
na
r
r
a
t
i
v
e
fo
r
ea
c
h
so
u
r
c
e
ar
e
a
an
d
do
w
n
g
r
a
d
i
e
n
t
fo
o
t
p
r
i
n
t
(f
l
o
w
sy
s
t
e
m
re
c
h
a
r
g
e
/
d
i
s
c
h
a
r
g
e
,
ho
r
i
z
o
n
t
a
l
fl
o
w
di
r
e
c
t
i
o
n
,
fl
o
w
pa
t
h
s
em
a
n
a
t
i
n
g
fr
o
m
al
l
si
d
e
s
(i
n
c
l
u
d
e
ma
p
)
.
CA
P
Pa
r
t
2 Se
c
t
i
o
n
2.
4
.
4
in
c
l
u
d
e
d
di
s
c
u
s
s
i
o
n
of
ge
o
c
h
e
m
i
c
a
l
pa
r
a
m
e
t
e
r
s
with consideration to whether
th
e
r
e
ar
e
tr
e
n
d
s
up
g
r
a
d
i
e
n
t
or
do
w
n
g
r
a
d
i
e
n
t
fr
o
m
th
e
so
u
r
c
e
.
Th
e
refined SCM also included flow paths
de
t
e
r
m
i
n
e
d
ac
r
o
s
s
th
e
en
t
i
r
e
si
t
e
.
Hy
d
r
o
g
e
o
l
o
g
i
c
a
n
d
O
t
h
e
r
Ge
o
c
h
e
m
i
c
a
l
C
o
n
c
e
p
t
u
a
l
Mo
d
e
l
s
45
Ex
p
l
a
i
n
im
p
l
i
c
a
t
i
o
n
s
of
ve
r
t
i
c
a
l
gr
a
d
i
e
n
t
s
in
re
c
h
a
r
g
e
an
d
di
s
c
h
a
r
g
e
ar
e
a
in
ea
c
h
so
u
r
c
e
ar
e
a
an
d
it
s
do
w
n
g
r
a
d
i
e
n
t
fo
o
t
p
r
i
n
t
.
Ve
r
t
i
c
a
l
hy
d
r
a
u
l
i
c
gr
a
d
i
e
n
t
s
we
r
e
ca
l
c
u
l
a
t
e
d
fo
r
Ro
u
n
d
2 da
t
a
,
an
d
were included in CAP Part 1. The
pa
t
t
e
r
n
s
in
ve
r
t
i
c
a
l
gr
a
d
i
e
n
t
s
ar
e
di
s
c
u
s
s
e
d
in
CA
P
Pa
r
t
2 Se
c
t
i
o
n
2.
3
.
1
.
1
.
Hy
d
r
o
g
e
o
l
o
g
i
c
a
n
d
O
t
h
e
r
Ge
o
c
h
e
m
i
c
a
l
C
o
n
c
e
p
t
u
a
l
Mo
d
e
l
s
46
In
c
l
u
d
e
ef
f
e
c
t
s
of
re
c
e
p
t
o
r
we
l
l
s
in
di
s
c
u
s
s
i
o
n
.
Al
s
o
in
c
l
u
d
e
po
s
s
i
b
l
e
im
p
a
c
t
s
fr
o
m
ba
s
i
n
to
re
c
e
p
t
o
r
s
in
co
n
c
e
p
t
u
a
l
mo
d
e
l
di
s
c
u
s
s
i
o
n
s
.
In
CA
P
Pa
r
t
2 Ap
p
e
n
d
i
x
C,
th
e
is
s
u
e
of
pu
m
p
i
n
g
we
l
l
s
is
di
s
c
u
s
s
e
d
.
Where appropriate, pumping wells are
in
c
l
u
d
e
d
as
an
in
f
l
u
e
n
c
e
in
th
e
gr
o
u
n
d
w
a
t
e
r
mo
d
e
l
.
Fo
r
ex
a
m
p
l
e
,
fo
r
the DEC Cliffside site, the pumping
we
l
l
s
we
r
e
n
'
t
mo
d
e
l
e
d
be
c
a
u
s
e
of
th
e
in
f
l
u
e
n
c
e
of
th
e
Br
o
a
d
Ri
v
e
r
.
Other DEC sites, such as Allen, Belews
Cr
e
e
k
,
an
d
Bu
c
k
,
th
e
pu
m
p
i
n
g
we
l
l
s
we
r
e
in
c
l
u
d
e
d
in
th
e
mo
d
e
l
.
Hy
d
r
o
g
e
o
l
o
g
i
c
a
n
d
O
t
h
e
r
Ge
o
c
h
e
m
i
c
a
l
C
o
n
c
e
p
t
u
a
l
Mo
d
e
l
s
47
Si
t
e
he
t
e
r
o
g
e
n
e
i
t
i
e
s
ar
e
no
t
ad
e
q
u
a
t
e
l
y
ex
p
l
a
i
n
e
d
.
Ex
p
l
a
i
n
ex
i
s
t
i
n
g
he
t
e
r
o
g
e
n
e
i
t
i
e
s
an
d
im
p
l
i
c
a
t
i
o
n
s
fo
r
fa
t
e
an
d
tr
a
n
s
p
o
r
t
mo
d
e
l
i
n
g
.
De
s
c
r
i
b
e
un
c
e
r
t
a
i
n
t
i
e
s
an
d
ex
p
l
a
i
n
im
p
a
c
t
of
un
c
e
r
t
a
i
n
t
i
e
s
.
Th
e
gr
o
u
n
d
w
a
t
e
r
mo
d
e
l
s
ar
e
be
i
n
g
up
d
a
t
e
d
an
d
re
c
a
l
i
b
r
a
t
e
d
in
c
l
u
d
i
n
g
new data as it has becoms available
as
pa
r
t
of
th
e
ex
p
a
n
d
e
d
gr
o
u
n
d
w
a
t
e
r
mo
d
e
l
do
m
a
i
n
ac
t
i
v
i
t
i
e
s
.
Un
c
e
r
t
a
i
n
i
t
i
e
s
and limitations will be
pr
e
s
e
n
t
e
d
as
pa
r
t
of
th
e
re
s
u
l
t
s
,
wh
i
c
h
ar
e
ex
p
e
c
t
e
d
to
be
co
m
p
l
e
t
e
d
during Fall 2016.
Hy
d
r
o
g
e
o
l
o
g
i
c
a
n
d
O
t
h
e
r
Ge
o
c
h
e
m
i
c
a
l
C
o
n
c
e
p
t
u
a
l
Mo
d
e
l
s
48
E
x
p
l
a
i
n
im
p
a
c
t
of
un
c
e
r
t
a
i
n
t
i
e
s
in
co
n
c
e
p
t
u
a
l
mo
d
e
l
.
Th
e
gr
o
u
n
d
w
a
t
e
r
mo
d
e
l
s
ar
e
be
i
n
g
up
d
a
t
e
d
an
d
re
c
a
l
i
b
r
a
t
e
d
in
c
l
u
d
i
n
g
new data as it has becoms available
as
pa
r
t
of
th
e
ex
p
a
n
d
e
d
gr
o
u
n
d
w
a
t
e
r
mo
d
e
l
do
m
a
i
n
ac
t
i
v
i
t
i
e
s
.
Un
c
e
r
t
a
i
n
i
t
i
e
s
and limitations will be
pr
e
s
e
n
t
e
d
as
pa
r
t
of
th
e
re
s
u
l
t
s
,
wh
i
c
h
ar
e
ex
p
e
c
t
e
d
to
be
co
m
p
l
e
t
e
d
during Fall 2016.
Hy
d
r
o
g
e
o
l
o
g
i
c
a
n
d
O
t
h
e
r
Ge
o
c
h
e
m
i
c
a
l
C
o
n
c
e
p
t
u
a
l
Mo
d
e
l
s
49
En
s
u
r
e
th
a
t
st
r
e
a
m
s
,
we
t
l
a
n
d
s
,
et
c
.
sh
o
w
n
in
Se
c
t
i
o
n
12
ar
e
in
c
l
u
d
e
d
on
al
l
fi
g
u
r
e
s
as
ne
e
d
e
d
.
In
c
l
u
d
e
in
co
n
c
e
p
t
u
a
l
mo
d
e
l
di
s
c
u
s
s
i
o
n
s
as
ap
p
r
o
p
r
i
a
t
e
.
CA
P
Pa
r
t
2 Se
c
t
i
o
n
2 fi
g
u
r
e
s
in
c
l
u
d
e
we
t
l
a
n
d
s
an
d
st
r
e
a
m
s
.
Hy
d
r
o
g
e
o
l
o
g
i
c
a
n
d
O
t
h
e
r
Ge
o
c
h
e
m
i
c
a
l
C
o
n
c
e
p
t
u
a
l
Mo
d
e
l
s
50
De
s
c
r
i
p
t
i
o
n
of
AM
E
C
ec
o
l
o
g
i
c
a
l
su
r
v
e
y
re
p
o
r
t
fi
n
d
i
n
g
s
no
t
ut
i
l
i
z
e
d
in
re
p
o
r
t
or
in
fi
g
u
r
e
s
.
Da
t
a
sh
o
u
l
d
be
us
e
d
,
sh
o
w
n
on
fi
g
u
r
e
s
or
ex
p
l
a
i
n
e
d
wh
y
no
t
.
Ec
o
l
o
g
i
c
a
l
da
t
a
co
n
c
e
r
n
i
n
g
ve
g
e
t
a
t
i
o
n
wa
s
in
c
l
u
d
e
d
in
th
e
CS
A
Se
c
t
i
o
n
12 Risk Assessment and referenced
in
th
e
Ec
o
‐Ch
e
c
k
l
i
s
t
s
pr
o
v
i
d
e
d
fo
r
ea
c
h
si
t
e
.
Pa
g
e
4 of
7
Dan River Steam Station CSA Supplement 2
Ta
b
l
e
2 ‐1:
Re
s
p
o
n
s
e
s
to
Gl
o
b
a
l
NC
D
E
Q
Co
m
m
e
n
t
s
Ty
p
e
Co
m
m
e
n
t
Nu
m
b
e
r
Co
m
m
e
n
t
G
e
n
e
r
a
l
Re
s
o
l
u
t
i
o
n
Mo
d
e
l
i
n
g
51
Ba
t
c
h
ge
o
c
h
e
m
i
c
a
l
mo
d
e
l
i
n
g
fo
r
ea
c
h
of
th
r
e
e
la
y
e
r
s
pe
r
co
n
s
t
i
t
u
e
n
t
wi
t
h
na
r
r
a
t
i
v
e
of
wh
a
t
ha
p
p
e
n
s
al
o
n
g
fl
o
w
pa
t
h
.
Se
l
e
c
t
fl
o
w
pa
t
h
al
i
g
n
m
e
n
t
wi
t
h
MO
D
PA
T
H
.
As
pr
o
v
i
d
e
d
in
CA
P
Pa
r
t
2 Mo
d
e
l
i
n
g
Ap
p
e
n
d
i
x
B,
Mo
d
e
l
Co
n
s
t
r
u
c
t
i
o
n
Section, each constituent was
mo
d
e
l
e
d
in
on
e
of
7 la
y
e
r
s
,
wh
i
c
h
fa
l
l
in
t
o
th
e
fo
l
l
o
w
i
n
g
ca
t
e
g
o
r
i
e
s
:
Ash material, Dike and ash storage
ma
t
e
r
i
a
l
,
Al
l
u
v
i
u
m
,
M1
Sa
p
r
o
l
i
t
e
,
M2
Sa
p
r
o
l
i
t
e
,
Tr
a
n
s
i
t
i
o
n
Zo
n
e
,
an
d
Fractured bedrock.
Mo
d
e
l
i
n
g
52
De
s
c
r
i
b
e
ge
o
c
h
e
m
i
c
a
l
co
n
d
i
t
i
o
n
s
an
d
me
c
h
a
n
i
s
m
s
,
an
d
ch
a
r
g
e
s
,
al
o
n
g
fl
o
w
pa
t
h
s
.
DE
Q
co
n
s
i
d
e
r
s
fl
o
w
pa
t
h
s
to
be
fr
o
m
th
e
ma
x
i
m
u
m
co
n
c
e
n
t
r
a
t
i
o
n
fo
r
a CO
I
to
a re
c
e
p
t
o
r
or
to
th
e
co
m
p
l
i
a
n
c
e
bo
u
n
d
a
r
y
.
MO
D
P
A
T
H
wa
s
us
e
d
to
id
e
n
t
i
f
y
an
d
de
l
i
n
e
a
t
e
fl
o
w
pa
t
h
s
.
Th
i
s
is
di
s
p
l
a
y
e
d
in CAP Part 2 Modeling Appendix
B,
Mo
d
e
l
Ca
l
i
b
r
a
t
i
o
n
in
th
e
pa
r
t
i
c
l
e
tr
a
c
k
i
n
g
fi
g
u
r
e
.
Mo
d
e
l
i
n
g
53
Mo
d
e
l
sh
o
u
l
d
us
e
hi
g
h
e
s
t
CO
P
C
in
so
u
r
c
e
ar
e
a
fo
r
mo
d
e
l
in
p
u
t
.
Th
e
r
e
wi
l
l
be
di
f
f
e
r
e
n
t
fl
o
w
pa
t
h
s
as
fl
o
w
pa
t
h
is
ba
s
e
d
on
ma
x
i
m
u
m
co
n
c
e
n
t
r
a
t
i
o
n
of
CO
I
.
Th
e
mo
d
e
l
pr
e
s
e
n
t
e
d
in
th
e
CA
P
Pa
r
t
2 Ap
p
e
n
d
i
x
B us
e
s
va
r
i
a
b
l
e
co
n
c
e
n
t
r
a
t
i
o
n
s
in the source areas to
ma
t
c
h
do
w
n
g
r
a
d
i
e
n
t
co
n
c
e
n
t
r
a
t
i
o
n
s
ob
s
e
r
v
e
d
in
mo
n
i
t
o
r
we
l
l
s
.
In
areas where the flow path from the
so
u
r
c
e
to
an
el
e
v
a
t
e
d
ob
s
e
r
v
e
d
co
n
c
e
n
t
r
a
t
i
o
n
in
a mo
n
i
t
o
r
we
l
l
is
observed, the highest measured source
co
n
c
e
n
t
r
a
t
i
o
n
is
us
e
d
in
th
e
mo
d
e
l
.
Mo
d
e
l
i
n
g
54
Im
p
a
c
t
s
fr
o
m
Fe
,
Mn
ar
e
no
t
re
l
a
t
e
d
to
K d – ho
w
wi
l
l
mo
d
e
l
i
n
g
ad
d
r
e
s
s
th
e
s
e
co
n
s
t
i
t
u
e
n
t
s
?
Th
e
gr
o
u
n
d
w
a
t
e
r
mo
d
e
l
do
e
s
no
t
ad
d
r
e
s
s
Fe
an
d
Mn
,
ho
w
e
v
e
r
th
e
geochemical modeling report does
tr
e
a
t
Fe
an
d
Mn
as
CO
I
s
(C
A
P
Pa
r
t
2 Ap
p
e
n
d
i
x
E)
,
an
d
de
t
e
r
m
i
n
e
s
th
e
forms they likely exist in under
co
n
d
i
t
i
o
n
s
at
th
e
re
s
p
e
c
t
i
v
e
si
t
e
s
(C
A
P
Pa
r
t
2 Ap
p
e
n
d
i
x
E Se
c
t
i
o
n
2:
Pourbaix diagrams).
Mo
d
e
l
i
n
g
55
Gr
o
u
n
d
w
a
t
e
r
mo
d
e
l
i
n
g
sh
o
u
l
d
us
e
si
t
e
sp
e
c
i
f
i
c
K d s.
So
r
p
t
i
o
n
te
r
m
s
we
r
e
de
v
e
l
o
p
e
d
an
d
ut
i
l
i
z
e
d
as
pa
r
t
of
th
e
gr
o
u
n
d
w
a
t
e
r
modeling presented in CAP Part 2,
Ap
p
e
n
d
i
x
B.
Mo
d
e
l
i
n
g
56
De
s
c
r
i
b
e
K d s an
d
HF
O
or
so
i
l
sa
m
p
l
e
s
in
ar
e
a
s
no
t
af
f
e
c
t
e
d
by
as
h
.
Ex
p
l
a
i
n
di
f
f
e
r
e
n
c
e
s
be
t
w
e
e
n
th
e
s
e
K d s an
d
K d s fr
o
m
im
p
a
c
t
e
d
ar
e
a
s
.
A un
i
f
o
r
m
Kd
va
l
u
e
fo
r
th
e
gr
o
u
n
d
w
a
t
e
r
mo
d
e
l
wa
s
ut
i
l
i
z
e
d
as
th
e
s
e
values are variable from sample to
sa
m
p
l
e
,
re
g
a
r
d
l
e
s
s
of
si
t
e
lo
c
a
t
i
o
n
(C
A
P
Pa
r
t
2,
Ap
p
e
n
d
i
x
A,
Gr
o
u
n
d
w
a
t
e
r
Model).
Mo
d
e
l
i
n
g
57
Gr
o
u
n
d
w
a
t
e
r
fl
o
w
mo
d
e
l
i
n
g
in
CA
P
ne
e
d
s
to
ac
c
o
u
n
t
fo
r
cu
m
u
l
a
t
i
v
e
ef
f
e
c
t
of
of
f
‐si
t
e
re
c
e
p
t
o
r
we
l
l
s
(i
.
e
.
,
wa
t
e
r
su
p
p
l
y
we
l
l
s
)
.
Ne
e
d
to
co
m
e
up
wi
t
h
so
m
e
as
s
u
m
p
t
i
o
n
s
re
g
a
r
d
i
n
g
de
p
t
h
an
d
yi
e
l
d
.
CS
A
re
p
o
r
t
s
ge
n
e
r
a
l
l
y
di
s
c
o
u
n
t
po
t
e
n
t
i
a
l
fo
r
up
g
r
a
d
i
e
n
t
fl
o
w
di
r
e
c
t
i
o
n
re
s
u
l
t
i
n
g
fr
o
m
of
f
‐si
t
e
pu
m
p
i
n
g
.
Mo
d
e
l
re
s
u
l
t
s
ne
e
d
to
be
in
c
l
u
d
e
d
in
th
e
CA
P
no
w
an
d
re
v
i
s
e
on
c
e
re
s
u
l
t
s
ar
e
in
fr
o
m
da
t
a
ga
p
we
l
l
s
th
a
t
ar
e
lo
c
a
t
e
d
to
he
l
p
in
f
o
r
m
gr
o
u
n
d
w
a
t
e
r
fl
o
w
di
r
e
c
t
i
o
n
ne
a
r
th
e
pr
o
p
e
r
t
y
bo
u
n
d
a
r
y
.
Th
e
cu
m
u
l
a
t
i
v
e
ef
f
e
c
t
of
of
f
‐si
t
e
re
c
e
p
t
o
r
we
l
l
s
we
r
e
ac
c
o
u
n
t
e
d
fo
r
in the groundwater modeling (CAP Part
2 Mo
d
e
l
i
n
g
Ap
p
e
n
d
i
x
B)
.
Th
e
yi
e
l
d
of
th
e
s
e
we
l
l
s
wa
s
es
t
i
m
a
t
e
d
at
400 gpd, which is the average EPA
ho
u
s
e
h
o
l
d
us
a
g
e
.
Th
e
gr
o
u
n
d
w
a
t
e
r
mo
d
e
l
s
ar
e
be
i
n
g
up
d
a
t
e
d
an
d
recalibrated including new data as it
ha
s
be
c
o
m
s
av
a
i
l
a
b
l
e
as
pa
r
t
of
th
e
ex
p
a
n
d
e
d
gr
o
u
n
d
w
a
t
e
r
mo
d
e
l
domain activities, including water supply
we
l
l
in
f
o
r
m
a
t
i
o
n
.
Un
c
e
r
t
a
i
n
i
t
i
e
s
an
d
li
m
i
t
a
t
i
o
n
s
wi
l
l
be
pr
e
s
e
n
t
e
d
as
part of the results, which are expected
to
be
co
m
p
l
e
t
e
d
du
r
i
n
g
Fa
l
l
20
1
6
.
Mo
d
e
l
i
n
g
58
A
d
d
r
e
s
s
hi
s
t
o
r
i
c
wa
t
e
r
le
v
e
l
s
in
po
n
d
in
gr
o
u
n
d
w
a
t
e
r
mo
d
e
l
i
n
g
.
Th
e
gr
o
u
n
d
w
a
t
e
r
mo
d
e
l
wa
s
ca
l
i
b
r
a
t
e
d
to
st
e
a
d
y
‐st
a
t
e
fl
o
w
co
n
d
i
t
i
o
n
s
and considered water levels from
su
m
m
e
r
20
1
5
.
Hi
s
t
o
r
i
c
wa
t
e
r
le
v
e
l
s
in
th
e
po
n
d
s
we
r
e
no
t
mo
d
e
l
e
d
.
The timing of start of the ash
op
e
r
a
t
i
o
n
s
in
di
f
f
e
r
e
n
t
ba
s
i
n
s
wa
s
co
n
s
i
d
e
r
e
d
in
th
e
gr
o
u
n
d
w
a
t
e
r
model. The groundwater models are
be
i
n
g
up
d
a
t
e
d
an
d
re
c
a
l
i
b
r
a
t
e
d
in
c
l
u
d
i
n
g
ne
w
da
t
a
as
it
ha
s
be
c
o
m
s
available as part of the expanded
gr
o
u
n
d
w
a
t
e
r
mo
d
e
l
do
m
a
i
n
ac
t
i
v
i
t
i
e
s
,
in
c
l
u
d
i
n
g
hi
s
t
o
r
i
c
wa
t
e
r
le
v
e
l
s
.
Mo
d
e
l
i
n
g
59
Ne
e
d
to
di
s
c
u
s
s
ho
w
gr
o
u
n
d
w
a
t
e
r
mo
d
e
l
re
s
u
l
t
s
ar
e
in
c
o
r
p
o
r
a
t
e
d
in
su
r
f
a
c
e
wa
t
e
r
mo
d
e
l
re
s
u
l
t
s
(i
n
c
l
u
d
i
n
g
ho
w
on
‐si
t
e
st
r
e
a
m
s
ar
e
in
c
o
r
p
o
r
a
t
e
d
)
.
Th
e
CA
P
Pa
r
t
1 Su
r
f
a
c
e
wa
t
e
r
mo
d
e
l
i
n
g
Ap
p
e
n
d
i
x
de
t
a
i
l
s
ho
w
gr
o
u
n
d
w
a
t
e
r
model results are incorporated
in
su
r
f
a
c
e
wa
t
e
r
mo
d
e
l
re
s
u
l
t
s
.
Mo
d
e
l
i
n
g
60
De
e
p
ro
c
k
gr
o
u
n
d
w
a
t
e
r
fl
o
w
no
t
we
l
l
pr
e
s
e
n
t
e
d
re
l
a
t
i
v
e
to
of
f
‐si
t
e
pu
m
p
i
n
g
.
Th
i
s
ne
e
d
s
to
be
pr
e
s
e
n
t
e
d
in
CA
P
.
Pa
r
t
i
c
l
e
fl
o
w
ma
p
s
th
a
t
ta
k
e
in
t
o
ac
c
o
u
n
t
of
f
s
i
t
e
pu
m
p
i
n
g
ar
e
pr
e
s
e
n
t
e
d
in the groundwater modeling
Ap
p
e
n
d
i
x
B of
th
e
CA
P
Pa
r
t
2.
Mo
d
e
l
i
n
g
61
Su
b
s
u
r
f
a
c
e
dr
a
i
n
a
g
e
sy
s
t
e
m
s
at
di
k
e
/
d
a
m
s
sh
o
u
l
d
be
sh
o
w
n
an
d
po
t
e
n
t
i
a
l
im
p
a
c
t
s
to
fa
t
e
& tr
a
n
s
p
o
r
t
mo
d
e
l
i
n
g
sh
o
u
l
d
be
co
n
s
i
d
e
r
e
d
.
Su
b
s
u
r
f
a
c
e
dr
a
i
n
a
g
e
sy
s
t
e
m
s
ar
e
sh
o
w
n
an
d
di
s
c
u
s
s
e
d
in
Se
c
t
i
o
n
4 of the CSA reports.
Pa
g
e
5 of
7
Dan River Steam Station CSA Supplement 2
Ta
b
l
e
2 ‐1:
Re
s
p
o
n
s
e
s
to
Gl
o
b
a
l
NC
D
E
Q
Co
m
m
e
n
t
s
Ty
p
e
Co
m
m
e
n
t
Nu
m
b
e
r
Co
m
m
e
n
t
G
e
n
e
r
a
l
Re
s
o
l
u
t
i
o
n
Da
t
a
P
r
e
s
e
n
t
a
t
i
o
n
62
Gu
i
d
e
l
i
n
e
s
re
q
u
i
r
e
– se
e
p
,
se
d
i
m
e
n
t
,
su
r
f
a
c
e
wa
t
e
r
,
re
c
e
p
t
o
r
we
l
l
da
t
a
,
re
s
u
l
t
s
sh
o
w
al
l
CO
I
s
(f
i
e
l
d
an
d
re
s
u
l
t
s
)
in
ch
e
m
bo
x
e
s
.
CA
P
Pa
r
t
2 in
c
l
u
d
e
d
ch
e
m
bo
x
ma
p
s
fo
r
se
e
p
s
,
se
d
i
m
e
n
t
s
,
su
r
f
a
c
e
water, and groundwater. Chem boxes for
re
c
e
p
t
o
r
we
l
l
s
we
r
e
no
t
ab
l
e
to
be
sh
o
w
n
sp
a
t
i
a
l
l
y
fo
r
al
l
sa
m
p
l
i
n
g
events, however, Figure 1 ‐3 in the CSA
Su
p
p
l
e
m
e
n
t
2 sh
o
w
s
lo
c
a
t
i
o
n
an
d
an
a
l
y
t
i
c
a
l
re
s
u
l
t
s
.
Da
t
a
P
r
e
s
e
n
t
a
t
i
o
n
63
Sh
o
w
co
n
c
e
n
t
r
a
t
i
o
n
s
ab
o
v
e
PQ
L
s
on
ch
e
m
bo
x
ma
p
s
,
no
t
ju
s
t
co
n
s
t
i
t
u
e
n
t
s
ab
o
v
e
2L
.
Ch
e
m
bo
x
ma
p
s
sh
o
w
al
l
de
t
e
c
t
e
d
co
n
s
t
i
t
u
e
n
t
s
fo
r
de
t
e
c
t
i
o
n
an
d
as
s
e
s
s
m
e
n
t
monitoring constituents as
pa
r
t
of
th
e
CA
P
Pa
r
t
2.
Da
t
a
P
r
e
s
e
n
t
a
t
i
o
n
64
A
d
d
ve
r
t
i
c
a
l
gr
a
d
i
e
n
t
s
to
fi
g
u
r
e
s
– pl
a
n
vi
e
w
.
CA
P
Pa
r
t
1 Se
c
t
i
o
n
3 in
c
l
u
d
e
d
fi
g
u
r
e
s
de
p
i
c
t
i
n
g
ve
r
t
i
c
a
l
gr
a
d
i
e
n
t
s
be
t
w
e
e
n
shallow and deep wells, and
be
t
w
e
e
n
de
e
p
an
d
be
d
r
o
c
k
we
l
l
s
.
Da
t
a
P
r
e
s
e
n
t
a
t
i
o
n
65
A
d
d
ve
r
t
i
c
a
l
gr
a
d
i
e
n
t
ma
p
s
.
CA
P
Pa
r
t
1 Se
c
t
i
o
n
3 in
c
l
u
d
e
s
fi
g
u
r
e
s
de
p
i
c
t
i
n
g
ve
r
t
i
c
a
l
gr
a
d
i
e
n
t
s
be
t
w
e
e
n
shallow and deep wells, and
be
t
w
e
e
n
de
e
p
an
d
be
d
r
o
c
k
we
l
l
s
.
Da
t
a
P
r
e
s
e
n
t
a
t
i
o
n
66
De
v
e
l
o
p
a po
t
e
n
t
i
o
m
e
t
r
i
c
su
r
f
a
c
e
ma
p
fo
r
th
e
tr
a
n
s
i
t
i
o
n
zo
n
e
we
l
l
s
.
De
e
p
fl
o
w
la
y
e
r
we
l
l
s
ar
e
us
e
d
to
in
v
e
s
t
i
g
a
t
e
th
e
tr
a
n
s
i
t
i
o
n
zo
n
e
,
an
d
potentiometric surfaces figures were
de
v
e
l
o
p
e
d
as
pa
r
t
of
th
e
CA
P
Pa
r
t
2 as
we
l
l
as
CS
A
Su
p
p
l
e
m
e
n
t
2.
Da
t
a
P
r
e
s
e
n
t
a
t
i
o
n
67
Sh
o
w
ca
t
i
o
n
‐an
i
o
n
ba
l
a
n
c
e
va
l
u
e
s
on
Pi
p
e
r
di
a
g
r
a
m
s
,
re
m
o
v
e
re
s
u
l
t
s
wi
t
h
ba
l
a
n
c
e
di
f
f
e
r
e
n
c
e
s
> 10
%
.
Pi
p
e
r
di
a
g
r
a
m
fi
g
u
r
e
s
ar
e
in
Se
c
t
i
o
n
10
of
th
e
CS
A
.
Up
d
a
t
e
d
pi
p
e
r
di
a
g
r
a
m
s
utilizing Round 5 data have
be
e
n
in
c
l
u
d
e
d
in
th
e
CS
A
Su
p
p
l
e
m
e
n
t
2 to
in
c
l
u
d
e
on
l
y
th
o
s
e
ev
e
n
t
s
with balance differences that are less
th
a
n
10
%
.
Da
t
a
P
r
e
s
e
n
t
a
t
i
o
n
68
Sh
o
w
al
l
re
c
e
p
t
o
r
we
l
l
s
on
fi
g
u
r
e
s
gi
v
e
n
th
e
ex
i
s
t
i
n
g
fi
g
u
r
e
ex
t
e
n
t
s
.
Fi
g
u
r
e
1 ‐3 in
th
e
CS
A
Su
p
p
l
e
m
e
n
t
2 pr
e
s
e
n
t
s
al
l
re
c
e
p
t
o
r
we
l
l
s
an
d
their analytical results. Those water
su
p
p
l
y
we
l
l
s
th
a
t
ca
n
be
sh
o
w
n
in
th
e
vi
e
w
p
o
r
t
s
of
th
e
th
e
po
t
e
n
t
i
o
m
e
t
r
i
c
surface and isoconcentration
fi
g
u
r
e
s
in
th
e
CS
A
Su
p
p
l
e
m
e
n
t
2 ar
e
al
s
o
in
c
l
u
d
e
d
.
Da
t
a
P
r
e
s
e
n
t
a
t
i
o
n
69
N
e
e
d
on
e
ma
p
wi
t
h
al
l
re
c
e
p
t
o
r
we
l
l
s
an
d
MW
s
.
F
i
g
u
r
e
1 ‐3 in
th
e
CS
A
Su
p
p
l
e
m
e
n
t
2 pr
e
s
e
n
t
s
al
l
re
c
e
p
t
o
r
we
l
l
s
an
d
their analytical results.
Da
t
a
P
r
e
s
e
n
t
a
t
i
o
n
70
S
h
o
w
se
e
p
re
s
u
l
t
s
wi
t
h
ch
e
m
bo
x
e
s
.
S
e
e
p
s
an
d
DE
Q
Se
e
p
s
we
r
e
pr
o
v
i
d
e
d
in
CA
P
Pa
r
t
1 Se
c
t
i
o
n
2 fi
g
u
r
e
s
.
Da
t
a
P
r
e
s
e
n
t
a
t
i
o
n
71
Sh
o
w
to
p
o
g
r
a
p
h
y
on
gr
o
u
n
d
w
a
t
e
r
su
r
f
a
c
e
co
n
t
o
u
r
ma
p
s
(a
d
d
el
e
v
a
t
i
o
n
la
b
e
l
s
to
co
n
t
o
u
r
s
)
.
To
p
o
g
r
a
p
h
y
ha
s
be
e
n
in
c
l
u
d
e
d
on
th
e
po
t
e
n
t
i
o
m
e
t
r
i
c
su
r
f
a
c
e
fi
g
u
r
e
s
provided in CSA Supplement 2.
Da
t
a
P
r
e
s
e
n
t
a
t
i
o
n
72
Ad
d
ge
o
l
o
g
i
c
da
t
a
an
d
is
o
‐co
n
c
e
n
t
r
a
t
i
o
n
da
t
a
(i
n
c
l
u
d
e
K d s)
on
cr
o
s
s
‐se
c
t
i
o
n
s
.
Cr
o
s
s
‐se
c
t
i
o
n
s
wi
l
l
be
ex
p
a
n
d
e
d
wi
t
h
ad
d
i
t
i
o
n
a
l
as
s
e
s
s
m
e
n
t
mo
n
i
t
o
r
i
n
g
wells for the CSA Supplement 2.
Th
e
s
e
wi
l
l
in
c
l
u
d
e
li
t
h
o
l
o
g
y
,
re
c
o
v
e
r
y
,
RQ
D
,
wh
e
r
e
av
a
i
l
a
b
l
e
,
as
we
l
l
as the vertical extent of COIs
Da
t
a
P
r
e
s
e
n
t
a
t
i
o
n
73
A
d
d
fi
g
u
r
e
sh
o
w
i
n
g
pH
,
Eh
,
et
c
.
re
s
u
l
t
s
.
C
A
P
Pa
r
t
1 Se
c
t
i
o
n
2 Ch
e
m
Bo
x
fi
g
u
r
e
s
in
c
l
u
d
e
d
fi
e
l
d
pa
r
a
m
e
t
e
r
s
.
Da
t
a
P
r
e
s
e
n
t
a
t
i
o
n
74
A
d
d
ta
b
l
e
w/
N
P
D
E
S
sa
m
p
l
e
ev
e
n
t
re
s
u
l
t
s
.
A
NP
D
E
S
sa
m
p
l
e
ev
e
n
t
s
re
s
u
l
t
s
ta
b
l
e
ha
s
be
e
n
pr
o
v
i
d
e
d
in
Se
c
t
i
o
n
1 of the CSA Supplement 2.
Da
t
a
P
r
e
s
e
n
t
a
t
i
o
n
75
Ch
e
m
bo
x
fi
g
u
r
e
s
fo
r
gr
o
u
n
d
w
a
t
e
r
– ad
d
ro
u
n
d
2 da
t
a
as
co
l
u
m
n
to
ri
g
h
t
of
ex
i
s
t
i
n
g
da
t
a
.
Ro
u
n
d
2 ch
e
m
b
o
x
fi
g
u
r
e
s
we
r
e
in
c
l
u
d
e
d
in
CA
P
Pa
r
t
2.
Da
t
a
P
r
e
s
e
n
t
a
t
i
o
n
76
Is
o
co
n
t
o
u
r
s
‐
Ne
e
d
to
ad
d
r
e
s
s
ho
w
is
o
co
n
t
o
u
r
li
n
e
s
ar
e
sh
o
w
n
on
fi
g
u
r
e
s
.
Sh
o
w
pa
r
t
of
th
e
li
n
e
as
da
s
h
e
d
wh
e
r
e
un
c
e
r
t
a
i
n
t
y
ex
i
s
t
s
(i
.
e
.
,
no
do
w
n
g
r
a
d
i
e
n
t
da
t
a
to
he
l
p
de
t
e
r
m
i
n
e
ex
t
e
n
t
of
is
o
co
n
t
o
u
r
)
.
De
p
i
c
t
co
n
c
e
n
t
r
a
t
i
o
n
s
ab
o
v
e
re
p
o
r
t
i
n
g
li
m
i
t
.
Ad
d
is
o
‐co
n
t
o
u
r
fi
g
u
r
e
fo
r
st
r
o
n
t
i
u
m
.
Is
o
c
o
n
c
e
n
t
r
a
t
i
o
n
ma
p
s
ut
i
l
i
z
i
n
g
Ro
u
n
d
5 an
a
l
y
t
i
c
a
l
re
s
u
l
t
s
,
in
c
l
u
d
i
n
g
strontium, where it is a COI, are
in
c
l
u
d
e
d
in
CS
A
Su
p
p
l
e
m
e
n
t
2.
Da
t
a
P
r
e
s
e
n
t
a
t
i
o
n
77
Ne
e
d
to
sh
o
w
na
t
u
r
a
l
re
s
o
u
r
c
e
in
f
o
r
m
a
t
i
o
n
(i
.
e
.
,
su
r
f
a
c
e
wa
t
e
r
fe
a
t
u
r
e
s
,
we
t
l
a
n
d
fe
a
t
u
r
e
s
,
he
r
o
n
ro
o
k
e
r
y
at
Bu
c
k
,
et
c
.
)
on
“b
a
s
e
ma
p
”
fi
g
u
r
e
s
.
CA
P
Pa
r
t
2 Se
c
t
i
o
n
2 fi
g
u
r
e
s
in
c
l
u
d
e
s
we
t
l
a
n
d
s
an
d
st
r
e
a
m
s
wh
i
c
h
were delineated by USACE. Other
na
t
u
r
a
l
re
s
o
u
r
c
e
s
we
r
e
in
c
l
u
d
e
d
on
fi
g
u
r
e
s
as
pa
r
t
of
th
e
Ec
o
‐Ch
e
c
k
l
i
s
t
referenced in Section 12 of the CSA.
Da
t
a
P
r
e
s
e
n
t
a
t
i
o
n
78
En
s
u
r
e
th
a
t
st
r
e
a
m
s
,
we
t
l
a
n
d
s
,
et
c
.
sh
o
w
n
in
Se
c
t
i
o
n
12
ar
e
in
c
l
u
d
e
d
on
al
l
fi
g
u
r
e
s
as
ne
e
d
e
d
.
CA
P
Pa
r
t
2 Se
c
t
i
o
n
2 fi
g
u
r
e
s
in
c
l
u
d
e
d
we
t
l
a
n
d
s
an
d
st
r
e
a
m
s
as
ne
e
d
e
d
.
Da
t
a
P
r
e
s
e
n
t
a
t
i
o
n
79
Mo
d
i
f
y
re
s
u
l
t
s
ta
b
l
e
s
to
in
c
l
u
d
e
fi
e
l
d
pa
r
a
m
e
t
e
r
s
DO
s
,
Eh
,
sp
e
c
co
n
d
u
c
t
a
n
c
e
,
pH
,
NT
U
in
al
l
re
s
u
l
t
s
ta
b
l
e
s
.
Fi
e
l
d
pa
r
a
m
e
t
e
r
s
we
r
e
in
c
l
u
d
e
d
on
th
e
CA
P
Pa
r
t
2 re
s
u
l
t
s
ta
b
l
e
s
,
re
f
e
r
e
n
c
e
d
in Section 2, as well as the CSA
Su
p
p
l
e
m
e
n
t
2 re
s
u
l
t
s
ta
b
l
e
s
,
re
f
e
r
e
n
c
e
d
in
Se
c
t
i
o
n
3.
Su
r
f
a
c
e
,
G
r
o
u
n
d
w
a
t
e
r
Di
s
c
h
a
r
g
e
80
De
s
c
r
i
b
e
SW
hy
d
r
o
l
o
g
y
(s
t
r
e
a
m
s
,
we
t
l
a
n
d
s
)
in
CA
P
an
d
ho
w
re
l
a
t
e
s
to
se
e
p
s
in
CS
M
.
CA
P
Pa
r
t
2,
Se
c
t
i
o
n
3 pe
r
t
a
i
n
s
to
th
e
Si
t
e
Co
n
c
e
p
t
u
a
l
mo
d
e
l
,
an
d
it
discusses surface water and seeps in
re
l
a
t
i
o
n
to
si
t
e
so
u
r
c
e
ar
e
a
s
.
Su
r
f
a
c
e
,
G
r
o
u
n
d
w
a
t
e
r
Di
s
c
h
a
r
g
e
81
Ch
e
c
k
fo
r
al
i
g
n
m
e
n
t
of
de
s
c
r
i
p
t
i
o
n
of
st
r
e
a
m
s
an
d
we
t
l
a
n
d
s
in
Se
c
t
i
o
n
12
.
CA
P
Pa
r
t
2,
Se
c
t
i
o
n
3 pe
r
t
a
i
n
s
to
th
e
Si
t
e
Co
n
c
e
p
t
u
a
l
mo
d
e
l
,
an
d
it
discusses surface water and seeps in
re
l
a
t
i
o
n
to
si
t
e
so
u
r
c
e
ar
e
a
s
.
Pa
g
e
6 of
7
Dan River Steam Station CSA Supplement 2
Ta
b
l
e
2 ‐1:
Re
s
p
o
n
s
e
s
to
Gl
o
b
a
l
NC
D
E
Q
Co
m
m
e
n
t
s
Ty
p
e
Co
m
m
e
n
t
Nu
m
b
e
r
Co
m
m
e
n
t
G
e
n
e
r
a
l
Re
s
o
l
u
t
i
o
n
Su
r
f
a
c
e
,
G
r
o
u
n
d
w
a
t
e
r
Di
s
c
h
a
r
g
e
82
S
h
o
w
al
l
su
r
f
a
c
e
wa
t
e
r
fe
a
t
u
r
e
s
on
ma
p
s
an
d
cr
o
s
s
se
c
t
i
o
n
s
.
CS
A
an
d
CA
P
si
t
e
ma
p
s
in
c
l
u
d
e
la
b
e
l
s
of
ma
j
o
r
su
r
f
a
c
e
wa
t
e
r
bo
d
i
e
s
at each site. In addition, the CSA
in
c
l
u
d
e
d
su
r
f
a
c
e
wa
t
e
r
in
f
o
r
m
a
t
i
o
n
in
Fi
g
u
r
e
4 ‐4:
Su
r
f
a
c
e
Wa
t
e
r
Bo
d
i
e
s
.
CAP Part 2 included Figure 3 ‐1: Site
Co
n
c
e
p
t
u
a
l
Mo
d
e
l
,
an
d
Fi
g
u
r
e
3 ‐2:
Cr
o
s
s
Se
c
t
i
o
n
wi
t
h
th
e
s
e
fe
a
t
u
r
e
s
.
Su
r
f
a
c
e
,
G
r
o
u
n
d
w
a
t
e
r
Di
s
c
h
a
r
g
e
83
A
d
d
wo
r
d
i
n
g
on
st
r
e
a
m
fl
o
w
me
a
s
u
r
e
m
e
n
t
s
pe
r
f
o
r
m
e
d
.
St
r
e
a
m
f
l
o
w
me
a
s
u
r
e
m
e
n
t
s
ha
v
e
be
e
n
in
c
o
r
p
o
r
a
t
e
d
in
t
o
th
e
ex
p
a
n
d
e
d
groundwater model domain
ac
t
i
v
i
t
i
e
s
.
Th
e
gr
o
u
n
d
w
a
t
e
r
mo
d
e
l
s
ar
e
be
i
n
g
up
d
a
t
e
d
an
d
re
c
a
l
i
b
r
a
t
e
d
including new data as it has
be
c
o
m
s
av
a
i
l
a
b
l
e
an
d
is
ex
p
e
c
t
e
d
to
be
co
m
p
l
e
t
e
d
du
r
i
n
g
Fa
l
l
20
1
6
.
Ri
s
k
A
s
s
e
s
s
m
e
n
t
84
In
c
l
u
d
e
no
n
‐tr
e
s
p
a
s
s
i
n
g
re
c
r
e
a
t
i
o
n
us
e
r
s
of
su
r
f
a
c
e
wa
t
e
r
an
d
dr
i
n
k
i
n
g
wa
t
e
r
we
l
l
re
c
e
p
t
o
r
s
.
In
th
e
st
a
n
d
‐al
o
n
e
Ri
s
k
As
s
e
s
s
m
e
n
t
re
p
o
r
t
,
re
c
r
e
a
t
i
o
n
a
l
sw
i
m
m
e
r
s
,
boaters, waders, and fishers are
in
c
l
u
d
e
d
in
th
e
re
c
e
p
t
o
r
s
,
as
ar
e
cu
r
r
e
n
t
/
f
u
t
u
r
e
of
f
‐si
t
e
re
s
i
d
e
n
t
s
.
In
addition, a separate risk assessment
ha
s
be
e
n
pr
o
v
i
d
e
d
su
b
s
e
q
u
e
n
t
to
th
e
CS
A
re
p
o
r
t
by
Du
k
e
En
e
r
g
y
vi
a
Haley & Aldritch.
Ri
s
k
A
s
s
e
s
s
m
e
n
t
85
Co
a
l
as
h
sh
o
u
l
d
be
in
c
l
u
d
e
d
as
pr
i
m
a
r
y
af
f
e
c
t
e
d
me
d
i
a
un
t
i
l
it
is
co
m
p
l
e
t
e
l
y
re
m
o
v
e
d
or
ot
h
e
r
w
i
s
e
ma
d
e
in
a
c
c
e
s
s
i
b
l
e
to
hu
m
a
n
co
n
t
a
c
t
.
Re
v
i
s
e
Ta
b
l
e
s
12
‐1,
12
‐2,
an
d
wo
r
d
i
n
g
in
Se
c
t
i
o
n
12
.
A se
p
a
r
a
t
e
ri
s
k
as
s
e
s
s
m
e
n
t
ha
s
be
e
n
pr
o
v
i
d
e
d
su
b
s
e
q
u
e
n
t
to
th
e
CS
A
report by Duke Energy via Haley &
Al
d
r
i
t
c
h
.
Ri
s
k
A
s
s
e
s
s
m
e
n
t
86
E
x
p
a
n
d
sp
e
c
i
a
t
i
o
n
re
s
u
l
t
s
di
s
c
u
s
s
i
o
n
wi
t
h
re
g
a
r
d
s
to
re
c
e
p
t
o
r
s
.
A se
p
a
r
a
t
e
ri
s
k
as
s
e
s
s
m
e
n
t
ha
s
be
e
n
pr
o
v
i
d
e
d
su
b
s
e
q
u
e
n
t
to
th
e
CS
A
report by Duke Energy via Haley &
Al
d
r
i
t
c
h
.
In
a
d
e
q
u
a
t
e
Da
t
a
– Al
l
So
u
r
c
e
Ar
e
a
s
87
Wh
e
r
e
2L
ex
c
e
e
d
a
n
c
e
s
in
t
e
r
c
e
p
t
ri
v
e
r
s
/
s
t
r
e
a
m
s
im
p
l
i
c
a
t
i
o
n
s
sh
o
u
l
d
be
di
s
c
u
s
s
e
d
.
Di
s
c
u
s
s
ve
r
t
i
c
a
l
gr
a
d
i
e
n
t
s
fo
r
we
l
l
pa
i
r
s
ad
j
a
c
e
n
t
to
ri
v
e
r
s
/
s
t
r
e
a
m
s
.
Ve
r
t
i
c
a
l
hy
d
r
a
u
l
i
c
gr
a
d
i
e
n
t
s
we
r
e
ca
l
c
u
l
a
t
e
d
fo
r
Ro
u
n
d
2 da
t
a
,
an
d
were included in CAP Part 1. The
pa
t
t
e
r
n
s
in
ve
r
t
i
c
a
l
gr
a
d
i
e
n
t
s
ar
e
di
s
c
u
s
s
e
d
in
CA
P
Pa
r
t
2 Se
c
t
i
o
n
2.
3
.
1
.
1
.
In
a
d
e
q
u
a
t
e
Da
t
a
– Al
l
So
u
r
c
e
Ar
e
a
s
88
If
a MW
do
e
s
no
t
ex
i
s
t
be
t
w
e
e
n
a 2L
ex
c
e
e
d
a
n
c
e
an
d
re
c
e
p
t
o
r
(s
t
r
e
a
m
an
d
wa
t
e
r
su
p
p
l
y
we
l
l
)
ad
d
i
t
i
o
n
a
l
we
l
l
s
or
tr
a
n
s
p
o
r
t
mo
d
e
l
i
n
g
is
ne
e
d
e
d
to
fi
l
l
da
t
a
ga
p
.
Du
k
e
En
e
r
g
y
ha
s
in
s
t
a
l
l
e
d
ad
d
i
t
i
o
n
a
l
mo
n
i
t
o
r
i
n
g
we
l
l
s
to
ad
d
r
e
s
s
co
n
c
e
r
n
s
to refine understanding of
ex
c
e
e
d
a
n
c
e
s
.
Re
s
u
l
t
s
fr
o
m
th
e
Ro
u
n
d
5,
in
c
l
u
d
i
n
g
ad
d
i
t
i
o
n
a
l
as
s
e
s
s
m
e
n
t
wells, has been included in CSA
Su
p
p
l
e
m
e
n
t
2.
In
a
d
e
q
u
a
t
e
Da
t
a
– Al
l
So
u
r
c
e
Ar
e
a
s
89
If
un
c
e
r
t
a
i
n
t
y
ex
i
s
t
s
ab
o
u
t
lo
c
a
l
fl
o
w
du
e
to
in
s
u
f
f
i
c
i
e
n
t
nu
m
b
e
r
or
pl
a
c
e
m
e
n
t
of
we
l
l
s
,
th
e
n
ad
d
i
t
i
o
n
a
l
we
l
l
s
sh
o
u
l
d
be
in
s
t
a
l
l
e
d
.
Sa
m
e
co
m
m
e
n
t
ap
p
l
i
e
s
fo
r
un
c
e
r
t
a
i
n
t
y
on
ve
r
t
i
c
a
l
gr
a
d
i
e
n
t
s
.
Du
k
e
En
e
r
g
y
ha
s
in
s
t
a
l
l
e
d
ad
d
i
t
i
o
n
a
l
mo
n
i
t
o
r
i
n
g
we
l
l
s
to
ad
d
r
e
s
s
co
n
c
e
r
n
s
to refine understanding of
ex
c
e
e
d
a
n
c
e
s
.
Re
s
u
l
t
s
fr
o
m
th
e
Ro
u
n
d
5,
in
c
l
u
d
i
n
g
ad
d
i
t
i
o
n
a
l
as
s
e
s
s
m
e
n
t
wells, has been included in CSA
Su
p
p
l
e
m
e
n
t
2.
Pa
g
e
7 of
7
Dan River Steam Station CSA Supplement 2
Ta
b
l
e
2 ‐2:
To
t
a
l
an
d
Ef
f
e
c
t
i
v
e
Po
r
o
s
i
t
y
an
d
Sp
e
c
i
f
i
c
St
o
r
a
g
e
by
Fl
o
w
La
y
e
r
Hy
d
r
o
s
t
r
a
t
i
g
r
a
p
h
i
c
U
n
i
t
Tr
a
n
s
i
t
i
o
n
Z
o
n
e
(
T
Z
)
Be
d
r
o
c
k
(
B
R
)
-
F
r
a
c
t
u
r
e
d
Be
d
r
o
c
k
(
B
R
)
-
D
e
n
s
e
No
t
e
s
:
3.
T
a
b
l
e
r
e
v
i
s
e
d
0
7
/
1
4
/
2
0
1
6
.
1.
R
a
n
g
e
s
b
a
s
e
d
o
n
p
u
b
l
i
s
h
e
d
v
a
l
u
e
s
(
D
o
m
e
n
i
c
o
a
n
d
M
i
f
f
l
i
n
,
1
9
6
5
;
S
i
n
g
h
a
l
a
n
d
G
u
p
t
a
,
2
0
1
0
)
.
2.
E
f
f
e
c
t
i
v
e
p
o
r
o
s
i
t
y
a
n
d
s
p
e
c
i
f
i
c
y
i
e
l
d
a
r
e
n
o
t
s
y
n
o
n
y
m
o
u
s
.
F
o
r
p
r
a
c
t
i
c
a
l
p
u
r
p
o
s
e
s
,
t
h
e
y
m
a
y
b
e
e
s
t
i
m
a
t
e
d
a
s
a
p
p
r
o
x
i
m
a
t
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Ta
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1
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R
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5
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NN
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N
N
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--
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Dan River Steam Station CSA Supplement 2
Ta
b
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3
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1
:
R
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5
A
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50
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50
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c
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.
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:
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Dan River Steam Station CSA Supplement 2
Ta
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3
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R
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5
A
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NN
N
N
N
N
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DR
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Dan River Steam Station CSA Supplement 2
Table 3‐4: Summary of Groundwater Elevations
Well Identification Date Top of Casing (TOC) Depth to Water (DTW) Groundwater Elevation
6/26/2015 47.28 492.14
9/2/2015 47.32 492.10
6/12/2016 46.65 492.77
6/26/2015 19.12 520.32
9/2/2015 19.40 520.04
6/12/2016 20.99 572.45
6/26/2015 40.58 498.84
9/2/2015 40.91 498.51
6/12/2016 40.93 498.49
6/26/2015 56.78 486.12
9/2/2015 57.05 485.85
6/12/2016 55.77 487.13
6/26/2015 51.46 491.51
9/2/2015 52.20 490.77
6/12/2016 48.81 494.16
6/26/2015 46.30 496.57
9/2/2015 47.39 495.48
6/12/2016 42.80 500.07
6/26/2015 39.37 489.90
9/2/2015 23.24 506.03
6/12/2016 40.44 488.77
6/26/2015 38.87 490.60
9/2/2015 38.92 490.55
6/12/2016 39.03 490.41
6/26/2015 15.16 514.18
9/2/2015 15.19 514.15
6/12/2016 17.13 512.15
6/26/2015 23.01 508.98
9/2/2015 22.46 509.53
6/12/2016 23.60 508.39
6/26/2015 12.29 521.56
9/2/2015 12.47 521.38
6/12/2016 13.33 520.52
6/26/2015 11.94 522.06
9/2/2015 12.12 521.88
6/12/2016 13.20 520.80
6/26/2015 21.78 570.06
9/2/2015 23.22 568.62
6/12/2016 ‐‐ ‐‐
6/26/2015 10.75 548.95
9/2/2015 11.54 548.16
6/12/2016 9.84 549.86
6/26/2015 32.68 528.32
9/2/2015 32.82 528.18
6/12/2016 29.99 531.04
AB‐30BR 529.27
AB‐30D 529.47
AB‐30S 529.34
AS‐10D 591.84
AS‐12S 559.70
AS‐2D 561.00
AB‐35BR 531.99
542.87
AB‐10D
AB‐10SL
AB‐10S
AB‐25BR
AB‐25D
AB‐25S
539.42
539.42
539.44
542.90
542.97
AB‐5D 533.85
AB‐5S 534.00
Page 1 of 7
Dan River Steam Station
CSA Supplement 2
Table 3‐4: Summary of Groundwater Elevations
Well Identification Date Top of Casing (TOC) Depth to Water (DTW) Groundwater Elevation
6/26/2015 17.50 544.67
9/2/2015 17.98 544.19
6/12/2016 ‐‐ ‐‐
6/26/2015 35.41 551.25
9/2/2015 36.31 550.35
6/12/2016 ‐‐ ‐‐
6/26/2015 36.71 545.39
9/2/2015 37.25 544.85
6/12/2016 34.09 548.01
6/26/2015 37.10 545.13
9/2/2015 37.57 544.66
6/12/2016 34.60 547.63
6/26/2015 16.02 500.38
9/2/2015 16.67 499.73
6/12/2016 15.68 500.72
6/26/2015 7.74 507.17
9/2/2015 7.89 507.02
6/12/2016 6.68 508.23
6/26/2015 7.95 507.29
9/2/2015 7.98 507.26
6/12/2016 6.61 508.63
6/29/2015 33.56 520.00
9/2/2015 33.67 519.89
6/12/2016 33.15 520.49
6/29/2015 30.33 523.07
9/2/2015 30.27 523.13
6/12/2016 ‐‐ ‐‐
6/26/2015 18.32 541.45
9/2/2015 19.65 540.12
6/12/2016 17.53 542.25
6/26/2015 19.78 540.35
9/2/2015 20.08 540.05
6/12/2016 18.28 541.84
6/29/2015 20.14 564.31
9/2/2015 21.05 563.40
6/12/2016 18.53 565.96
6/29/2015 12.41 572.49
9/2/2015 13.70 571.20
6/12/2016 11.90 573.03
6/26/2015 6.54 493.65
9/2/2015 6.17 494.02
6/12/2016 6.02 494.17
6/26/2015 10.92 489.05
9/2/2015 9.22 490.75
6/12/2016 9.02 490.95
AS‐4D 562.17
AS‐6D 586.66
AS‐8BR 582.10
BG‐5S 515.24
GWA‐10D 553.56
GWA‐10S 553.40
AS‐8D 582.23
BG‐1D 516.40
BG‐5D 514.91
GWA‐12S 584.90
GWA‐14D 500.19
GWA‐11D 559.77
GWA‐11S 560.13
GWA‐12D 584.45
GWA‐14S 499.97
Page 2 of 7
Dan River Steam Station
CSA Supplement 2
Table 3‐4: Summary of Groundwater Elevations
Well Identification Date Top of Casing (TOC) Depth to Water (DTW) Groundwater Elevation
6/26/2015 22.60 481.53
9/2/2015 22.82 481.31
6/12/2016 21.91 482.22
6/26/2015 DRY ‐‐
9/2/2015 DRY ‐‐
6/12/2016 DRY ‐‐
6/29/2015 30.57 571.01
9/2/2015 32.09 569.49
6/12/2016 27.00 574.58
6/29/2015 28.81 572.58
9/2/2015 32.25 569.14
6/12/2016 24.88 576.51
6/26/2015 27.76 560.28
9/2/2015 29.17 558.87
6/12/2016 ‐‐ ‐‐
6/26/2015 23.45 564.12
9/2/2015 25.00 562.57
6/12/2016 ‐‐ ‐‐
6/26/2015 24.22 549.82
9/2/2015 24.72 549.32
6/12/2016 ‐‐ ‐‐
6/26/2015 21.02 552.96
9/2/2015 21.32 552.66
6/12/2016 ‐‐ ‐‐
6/26/2015 27.25 499.95
9/2/2015 27.05 500.15
6/12/2016 27.59 499.61
6/26/2015 21.99 505.88
9/2/2015 21.78 506.09
6/12/2016 22.76 505.11
6/26/2015 3.43 496.30
9/2/2015 3.11 496.62
6/12/2016 3.10 496.63
6/26/2015 17.94 483.26
9/2/2015 17.48 483.72
6/12/2016 16.35 484.85
6/26/2015 13.53 487.95
9/2/2015 14.54 486.94
6/12/2016 12.54 488.94
6/26/2015 17.33 526.15
9/2/2015 18.61 524.87
6/12/2016 16.18 527.30
6/26/2015 16.08 527.08
9/2/2015 17.58 525.58
6/12/2016 14.94 528.22
GWA‐15D 504.13
GWA‐3D 574.04
GWA‐3S 573.98
GWA‐4D 527.20
GWA‐15S 504.21
GWA‐1D 601.58
GWA‐2S 587.57
GWA‐1S 601.39
GWA‐2D 588.04
GWA‐4S 527.87
GWA‐5BR 499.73
GWA‐7S 543.16
GWA‐6S 501.48
GWA‐7D 543.48
501.20GWA‐6D
Page 3 of 7
Dan River Steam Station
CSA Supplement 2
Table 3‐4: Summary of Groundwater Elevations
Well Identification Date Top of Casing (TOC) Depth to Water (DTW) Groundwater Elevation
6/26/2015 16.26 567.75
9/2/2015 17.28 566.73
6/12/2016 14.06 569.95
6/26/2015 15.35 568.52
9/2/2015 15.86 568.01
6/12/2016 12.93 570.94
6/29/2015 30.93 580.37
9/2/2015 32.15 579.15
6/12/2016 26.78 584.52
6/29/2015 30.22 581.50
9/2/2015 31.42 580.30
6/12/2016 25.65 586.07
6/29/2015 ‐‐ ‐‐
9/2/2015 DRY ‐‐
6/12/2016 DRY ‐‐
6/29/2015 50.05 482.00
9/2/2015 50.61 481.44
6/12/2016 49.15 482.65
6/29/2015 ‐‐ ‐‐
9/2/2015 ‐‐ ‐‐
6/12/2016 DRY ‐‐
6/29/2015 DRY ‐‐
9/2/2015 38.70 493.13
6/12/2016 38.31 492.85
6/29/2015 20.91 572.68
9/2/2015 22.42 571.17
6/12/2016 19.22 574.37
6/29/2015 20.52 572.71
9/2/2015 22.08 571.15
6/12/2016 17.87 575.36
6/29/2015 4.13 558.10
9/2/2015 5.10 557.13
6/12/2016 ‐‐ ‐‐
6/29/2015 5.78 556.50
9/2/2015 6.54 555.74
6/12/2016 ‐‐ ‐‐
6/29/2015 2.35 496.55
9/2/2015 1.88 497.02
6/12/2016 ‐‐ ‐‐
6/29/2015 5.42 493.38
9/2/2015 5.06 493.74
6/12/2016 ‐‐ ‐‐
6/26/2015 15.82 486.50
9/2/2015 16.26 486.06
6/12/2016 14.19 488.13
MW‐11D 531.83
GWA‐8D 584.01
MW‐10 531.81
MW‐10D 532.05
MW‐11 531.16
GWA‐8S 583.87
GWA‐9D 611.30
GWA‐9S 611.72
MW‐20S 562.28
MW‐21D 498.90
MW21S 498.80
MW‐12 593.59
MW‐12D 593.23
MW‐20D 562.23
MW‐22BR 502.32
Page 4 of 7
Dan River Steam Station
CSA Supplement 2
Table 3‐4: Summary of Groundwater Elevations
Well Identification Date Top of Casing (TOC) Depth to Water (DTW) Groundwater Elevation
6/29/2015 38.96 465.56
9/2/2015 DRY ‐‐
6/12/2016 ‐‐ ‐‐
6/29/2015 20.42 484.77
9/2/2015 20.89 484.30
6/12/2016 ‐‐ ‐‐
6/26/2015 FLOWING ARTESIAN ‐‐
9/2/2015 FLOWING ARTESIAN ‐‐
6/12/2016 FLOWING ARTESIAN ‐‐
6/29/2015 14.75 513.47
9/2/2015 14.12 514.10
6/12/2016 12.75 515.47
6/29/2015 22.91 570.64
9/2/2015 24.10 569.45
6/12/2016 ‐‐ ‐‐
6/26/2015 93.52 557.85
9/2/2015 93.74 557.63
6/12/2016 ‐‐ ‐‐
6/26/2015 69.28 544.34
9/2/2015 69.81 543.81
6/12/2016 ‐‐ ‐‐
6/26/2015 11.51 521.08
9/2/2015 11.45 521.14
6/12/2016 12.45 520.14
6/26/2015 17.43 521.48
9/2/2015 17.36 521.55
6/12/2016 17.72 521.19
6/26/2015 41.85 495.88
9/2/2015 42.22 495.51
6/12/2016 41.14 496.59
6/26/2015 29.30 510.45
9/2/2015 29.67 510.08
6/12/2016 27.20 512.55
6/26/2015 45.18 525.57
9/2/2015 45.58 525.17
6/12/2016 45.29 525.46
6/26/2015 24.18 547.75
9/2/2015 24.38 547.55
6/12/2016 21.94 549.99
6/26/2015 30.49 536.72
9/2/2015 30.72 536.49
6/12/2016 29.36 537.85
6/29/2015 20.39 506.02
9/2/2015 DRY ‐‐
6/12/2016 DRY ‐‐
MW‐22S 505.19
MW‐23D 528.22
MW‐301BR 593.55
MW‐22D 504.52
MW‐23BR 527.55
MW‐310BR 538.91
MW‐311BR 537.73
MW‐314BR 539.75
MW‐303BR 651.37
MW‐306BR 613.62
MW‐308BR 532.59
MW‐9 526.41
MW‐315BR 570.75
MW‐317BR 571.93
MW‐318D 567.21
Page 5 of 7
Dan River Steam Station
CSA Supplement 2
Table 3‐4: Summary of Groundwater Elevations
Well Identification Date Top of Casing (TOC) Depth to Water (DTW) Groundwater Elevation
6/29/2015 33.19 493.85
9/2/2015 34.24 492.80
6/12/2016 31.57 495.47
6/29/2015 10.42 583.57
9/2/2015 112.72 481.27
‐‐ ‐‐ ‐‐
6/26/2015 36.80 549.73
9/2/2015 11.31 575.22
‐‐ ‐‐ ‐‐
6/26/2015 79.41 571.02
9/2/2015 29.66 620.77
‐‐ ‐‐ ‐‐
6/29/2015 9.92 550.30
‐‐ ‐‐ ‐‐
‐‐ ‐‐ ‐‐
6/26/2015 14.56 546.30
9/2/2015 11.62 549.24
‐‐ ‐‐ ‐‐
6/26/2015 12.97 548.25
9/2/2015 11.45 549.77
‐‐ ‐‐ ‐‐
6/29/2015 63.04 548.11
9/2/2015 14.14 597.01
‐‐ ‐‐ ‐‐
6/29/2015 51.23 558.62
9/2/2015 13.27 596.58
‐‐ ‐‐ ‐‐
6/29/2015 18.23 516.65
9/2/2015 13.66 521.22
‐‐ ‐‐ ‐‐
6/29/2015 6.14 525.15
9/2/2015 6.75 524.54
‐‐ ‐‐ ‐‐
6/29/2015 7.54 521.48
9/2/2015 4.07 524.95
‐‐ ‐‐ ‐‐
6/29/2015 19.62 519.70
9/2/2015 ‐‐ ‐‐
‐‐ ‐‐ ‐‐
6/29/2015 22.12 514.63
9/2/2015 29.66 507.09
‐‐ ‐‐ ‐‐
6/29/2015 ‐‐ ‐‐
9/2/2015 27.55 496.19
‐‐ ‐‐ ‐‐
MW‐9D 527.04
OW‐301D 593.99
OW‐304D 560.22
OW‐305D 560.86
OW‐305S 561.22
OW‐302D 586.53
OW‐303D 650.43
OW‐311D 536.75
OW‐312D 523.74
OW‐306D 611.15
OW‐306S 609.85
OW‐310S 539.32
OW‐307D
OW‐309D
534.88
529.02
OW‐308D 531.29
Page 6 of 7
Dan River Steam Station
CSA Supplement 2
Table 3‐4: Summary of Groundwater Elevations
Well Identification Date Top of Casing (TOC) Depth to Water (DTW) Groundwater Elevation
6/29/2015 27.62 497.04
‐‐ ‐‐
‐‐ ‐‐
6/29/2015 28.93 506.93
9/2/2015 3.20 532.66
‐‐ ‐‐ ‐‐
6/29/2015 32.21 509.09
9/2/2015 10.65 530.65
‐‐ ‐‐ ‐‐
6/29/2015 DRY ‐‐
9/2/2015 62.19 478.69
‐‐ ‐‐ ‐‐
6/29/2015 22.12 547.17
9/2/2015 19.89 549.40
‐‐ ‐‐ ‐‐
6/29/2015 15.49 553.76
9/2/2015 3.09 566.16
‐‐ ‐‐ ‐‐
6/29/2015 15.28 557.58
9/2/2015 6.13 566.73
‐‐ ‐‐ ‐‐
6/29/2015 29.78 537.38
9/2/2015 1.80 565.36
‐‐ ‐‐ ‐‐
6/29/2015 DRY ‐‐
9/2/2015 2.30 579.38
‐‐ ‐‐ ‐‐
6/29/2015 23.98 558.09
9/2/2015 55.56 526.51
‐‐ ‐‐ ‐‐
6/29/2015 3.00 607.39
9/2/2015 DRY ‐‐
‐‐ ‐‐ ‐‐
6/26/2015 11.06 580.95
9/2/2015 55.34 536.67
‐‐ ‐‐ ‐‐
OW‐313D 535.86
OW‐320D
OW‐321D
540.88
569.29
OW‐319S 582.07
OW‐312S 524.66
OW‐314D 541.30
OW‐318BR 567.16
OW‐319D 581.68
610.39
592.01
OW‐315S
OW‐317D
569.25
572.86
OW‐314S
OW‐315D
Page 7 of 7
Dan River Steam Station
CSA Supplement 2
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2
.
56
6
.
1
0
2
9
5
.
7
4
.
7
7
3
1
5
.
2
1
.
2
5
1
0
0
1
6
.
3
0
.
7
0
9
6
.
7
3
3
4
.
9
%
AB
-
3
0
D
G
r
o
u
n
d
w
a
t
e
r
4
/
2
5
/
2
0
1
6
0
0
1
2
0
1
.
9
6
7
2
0
.
9
0
.
5
8
9
0
0
9
2
1
.
91
5
4
.
4
7
1
6
4
.
8
3
.
2
3
2
1
0
.
9
0
.
8
9
7
0
0
1
3
.
6
0
.
5
9
1
4
.
7
2
2
.
7
%
AB
-
3
0
S
G
r
o
u
n
d
w
a
t
e
r
4
/
2
5
/
2
0
1
6
0
0
5
.
3
0
.
0
8
7
1
0
0
.
2
8
2
0
0
8
2
.
7
1
.
72
1
2
.
0
9
8
.
9
4
0
.
4
4
6
5
.
5
8
0
.
4
5
9
0
0
2
5
.
4
1
.
1
0
4
2
.
0
0
9
-
2
.
0
%
AB
-
3
5
B
R
G
r
o
u
n
d
w
a
t
e
r
4
/
2
6
/
2
0
1
6
0
0
2
5
4
4
.
1
6
4
1
1
.
7
0
.
3
3
0
0
1
2
1
2
.
5
1
8
7.
0
1
2
9
3
.
2
4
.
6
4
8
1
8
.
3
1
.
5
0
6
1
5
.
3
0
.
3
9
1
2
6
.
2
1
.
1
3
9
7
.
6
8
4
4
.
6
%
AB
-
5
D
G
r
o
u
n
d
w
a
t
e
r
4
/
2
5
/
2
0
1
6
0
0
1
7
6
2
.
8
8
5
1
9
.
6
0
.
5
5
2
0
0
7
7
.
5
1
.
6
1
3
5.
0
5
6
5
.
9
3
.
2
8
7
1
3
.
8
1
.
1
3
6
3
.
9
7
0
.
1
0
2
2
0
0
.
8
7
5
.
3
9
5
3
.
3
%
AS
-
1
2
S
G
r
o
u
n
d
w
a
t
e
r
4
/
2
6
/
2
0
1
6
0
0
1
8
4
3
.
0
1
6
1
8
.
1
0
.
5
1
0
.
0
2
4
0
7
8
.
3
1
.6
3
5
.
1
5
6
3
7
.
9
1
.
8
9
3
0
.
3
2
.
4
9
4
0
0
3
1
.
5
1
.
3
7
5
.
7
5
4
5
.
5
%
AS
-
2
D
G
r
o
u
n
d
w
a
t
e
r
4
/
2
6
/
2
0
1
6
0
0
2
5
1
4
.
1
1
5
1
7
.
5
0
.
4
9
3
0
0
1
7
9
3
.
7
2
5
8
.
33
3
9
9
.
4
4
.
9
5
8
3
3
.
2
2
.
7
3
3
2
.
6
3
0
.
0
6
7
2
8
.
4
1
.
2
3
5
8
.
9
9
3
3
.
8
%
AS
-
8
B
R
G
r
o
u
n
d
w
a
t
e
r
4
/
2
5
/
2
0
1
6
0
0
1
7
2
2
.
8
2
6
.
8
0
.
1
9
2
0
0
6
9
.
5
1
.
44
6
4
.
4
5
8
6
5
3
.
2
4
2
1
0
.
2
0
.
8
4
3
.
1
5
0
.
0
8
1
1
3
.
8
0
.
6
4
.
7
6
3
3
.
3
%
AS
-
8
D
G
r
o
u
n
d
w
a
t
e
r
4
/
2
5
/
2
0
1
6
0
0
1
2
0
1
.
9
6
7
5
.
3
0
.
1
4
9
0
0
2
0
.
9
0
.
43
5
2
.
5
5
1
2
7
.
6
1
.
3
7
7
9
.
5
9
0
.
7
8
9
0
0
1
3
.
9
0
.
6
0
4
2
.
7
7
4
.
1
%
BG
-
1
D
G
r
o
u
n
d
w
a
t
e
r
4
/
4
/
2
0
1
6
1
2
.
1
0
.
4
0
3
6
0
.
3
0
.
9
8
9
5
.
9
0
.
1
6
6
0
.
2
2
0
.
00
4
1
0
6
2
.
2
0
6
3
.
7
6
8
3
6
.
1
1
.
8
1
1
.
2
0
.
9
2
2
4
.
9
0
.
1
2
5
2
9
.
3
1
.
2
7
4
4
.
1
2
1
4
.
5
%
BG
-
5
D
G
r
o
u
n
d
w
a
t
e
r
3
/
2
8
/
2
0
1
6
0
0
1
1
6
1
.
9
0
2
6
.
2
0
.
1
7
5
0
.
2
4
0
.
0
0
4
34
.
1
0
.
7
1
2
.
7
9
1
2
5
1
.
2
4
7
1
4
.
7
1
.
2
1
0
0
1
7
.
8
0
.
7
7
4
3
.
2
3
1
7
.
3
%
BG
-
5
D
G
r
o
u
n
d
w
a
t
e
r
4
/
4
/
2
0
1
6
0
0
1
1
6
1
.
9
0
2
6
.
2
0
.
1
7
5
0
.
2
4
0
.
0
0
4
34
.
1
0
.
7
1
2
.
7
9
1
2
5
1
.
2
4
7
1
4
.
7
1
.
2
1
0
0
1
7
.
8
0
.
7
7
4
3
.
2
3
1
7
.
3
%
BG
-
5
S
G
r
o
u
n
d
w
a
t
e
r
3
/
2
8
/
2
0
1
6
0
0
7
3
.
6
1
.
2
0
7
6
.
7
0
.
1
8
9
0
.
4
6
0
.
0
0
7
33
.
6
0
.
6
9
9
2
.
1
0
2
1
6
.
8
0
.
8
3
8
1
1
.
4
0
.
9
3
8
0
0
1
7
0
.
7
3
9
2
.
5
1
5
8
.
9
%
GW
A
-
1
0
D
G
r
o
u
n
d
w
a
t
e
r
4
/
2
6
/
2
0
1
6
0
0
6
8
1
.
1
1
5
9
.
3
0
.
2
6
2
0
.
2
4
0
.
0
0
4
6
1
.
2
1
.
2
7
4
2
.
6
5
5
2
2
.
9
1
.
1
4
2
1
2
.
5
1
.
0
2
9
0
0
1
5
.
6
0
.
6
7
8
2
.
8
4
9
3
.
5
%
GW
A
-
1
1
D
G
r
o
u
n
d
w
a
t
e
r
4
/
2
6
/
2
0
1
6
0
0
1
7
6
2
.
8
8
5
1
1
.
2
0
.
3
1
5
0
0
4
0
.
5
0
.8
4
3
4
.
0
4
3
5
0
.
5
2
.
5
1
9
1
7
.
1
1
.
4
0
7
0
0
1
6
.
6
0
.
7
2
2
4
.
6
4
8
7
.
0
%
GW
A
-
1
1
S
G
r
o
u
n
d
w
a
t
e
r
4
/
2
6
/
2
0
1
6
0
0
2
5
.
1
0
.
4
1
1
1
0
.
4
0
.
2
9
3
0
.
3
1
0
.
0
0
5
4.
7
0
.
0
9
8
0
.
8
0
7
5
.
4
7
0
.
2
7
3
2
.
8
0
.
2
3
0
0
9
.
5
3
0
.
4
1
4
0
.
9
1
7
6
.
4
%
GW
A
-
1
2
D
G
r
o
u
n
d
w
a
t
e
r
3
/
2
8
/
2
0
1
6
0
0
2
0
1
3
.
2
9
5
4
0
.
1
1
3
0
.
1
0
.
0
0
2
1
9
.
6
0
.
4
0
8
3
.
8
1
8
5
0
.
9
2
.
5
3
9
1
7
.
8
1
.
4
6
5
0
0
9
.
6
9
0
.
4
2
1
4
.
4
2
5
7
.
4
%
GW
A
-
1
2
S
G
r
o
u
n
d
w
a
t
e
r
3
/
2
8
/
2
0
1
6
0
0
9
.
7
0
.
1
5
9
3
.
3
0
.
0
9
3
1
.
5
0
.
0
2
4
24
.
9
0
.
5
1
8
0
.
7
9
4
6
.
7
6
0
.
3
3
7
4
.
1
6
0
.
3
4
2
0
0
5
.
7
2
0
.
2
4
9
0
.
9
2
8
7
.
8
%
GW
A
-
1
4
D
G
r
o
u
n
d
w
a
t
e
r
4
/
2
5
/
2
0
1
6
0
0
1
5
7
2
.
5
7
4
1
2
.
1
0
.
3
4
1
0
.
0
2
1
0
10
6
2
.
2
0
6
5
.
1
2
1
7
8
.
2
3
.
9
8
.
1
5
0
.
6
7
1
0
0
2
1
.
9
0
.
9
5
2
5
.
5
2
3
3
.
8
%
GW
A
-
1
4
S
G
r
o
u
n
d
w
a
t
e
r
4
/
2
5
/
2
0
1
6
0
0
4
5
.
4
0
.
7
4
4
5
.
5
0
.
1
5
5
0
.
1
2
0
.
0
0
2
2
1
.
9
0
.
4
5
6
1
.
3
5
7
8
.
9
7
0
.
4
4
7
4
.
7
8
0
.
3
9
3
0
0
9
.
5
3
0
.
4
1
4
1
.
2
5
4
-
3
.
9
%
GW
A
-
1
4
S
G
r
o
u
n
d
w
a
t
e
r
4
/
2
6
/
2
0
1
6
0
0
4
5
.
4
0
.
7
4
4
5
.
5
0
.
1
5
5
0
.
1
2
0
.
0
0
2
2
1
.
9
0
.
4
5
6
1
.
3
5
7
8
.
9
7
0
.
4
4
7
4
.
7
8
0
.
3
9
3
0
0
9
.
5
3
0
.
4
1
4
1
.
2
5
4
-
3
.
9
%
GW
A
-
1
5
D
G
r
o
u
n
d
w
a
t
e
r
4
/
2
5
/
2
0
1
6
0
0
1
1
8
1
.
9
3
4
1
0
.
5
0
.
2
9
6
0
.
0
3
6
0
.
0
0
1
14
8
3
.
0
8
5
.
3
1
1
7
2
3
.
5
9
1
1
5
1
.
2
3
5
4
.
3
1
0
.
1
1
1
7
0
.
7
3
9
5
.
6
7
5
3
.
3
%
GW
A
-
1
D
G
r
o
u
n
d
w
a
t
e
r
4
/
2
6
/
2
0
1
6
2
1
9
7
.
3
0
0
3
.
6
0
.
1
0
1
0
0
2
0
0.
4
1
6
7
.
8
1
7
1
4
0
.
6
9
8
0
0
2
0
9
5
.
3
4
5
6
3
2
.
7
3
9
8
.
7
8
2
5
.
8
%
GW
A
-
1
S
G
r
o
u
n
d
w
a
t
e
r
4
/
2
5
/
2
0
1
6
0
0
5
5
.
8
0
.
9
1
5
2
0
.
0
5
6
0
.
0
3
0
3
.
2
0.
0
6
7
1
.
0
3
8
2
.
9
6
0
.
1
4
8
3
.
7
6
0
.
3
0
9
0
0
1
6
.
5
0
.
7
1
7
1
.
1
7
4
6
.
1
%
GW
A
-
4
D
G
r
o
u
n
d
w
a
t
e
r
4
/
2
6
/
2
0
1
6
0
0
4
1
.
8
0
.
6
8
5
1
2
.
1
0
.
3
4
1
0
0
4
2
.
5
0
.8
8
4
1
.
9
1
1
5
.
5
0
.
7
7
3
6
.
3
3
0
.
5
2
1
0
0
1
8
.
1
0
.
7
8
7
2
.
0
8
1
4
.
3
%
GW
A
-
4
S
G
r
o
u
n
d
w
a
t
e
r
4
/
2
6
/
2
0
1
6
0
0
5
0
.
4
0
.
8
2
6
7
.
9
0
.
2
2
3
0
0
4
7
0
.
9
7
8
2.
0
2
7
2
1
.
2
1
.
0
5
7
5
.
5
6
0
.
4
5
8
4
.
1
3
0
.
1
0
6
1
4
.
1
0
.
6
1
3
2
.
2
3
4
4
.
9
%
GW
A
-
5
B
R
G
r
o
u
n
d
w
a
t
e
r
4
/
2
6
/
2
0
1
6
0
0
1
6
5
2
.
7
0
5
1
7
.
6
0
.
4
9
6
0
0
4
1
9
8.
7
2
1
1
.
9
2
1
1
8
4
9
.
1
7
7
2
4
.
5
2
.
0
1
6
0
0
1
9
.
8
0
.
8
6
1
1
2
.
0
5
4
0
.
6
%
GW
A
-
6
D
G
r
o
u
n
d
w
a
t
e
r
4
/
2
5
/
2
0
1
6
0
0
1
2
1
1
.
9
8
4
1
8
.
1
0
.
5
1
0
0
6
1
1
.
2
7
3
.
7
6
4
4
0
.
1
2
1
1
0
.
9
0
5
0
0
2
7
1
.
1
7
4
4
.
0
7
9
4
.
0
%
GW
A
-
6
S
G
r
o
u
n
d
w
a
t
e
r
4
/
2
5
/
2
0
1
6
0
0
2
4
8
4
.
0
6
6
1
4
.
9
0
.
4
2
0
0
1
0
.
4
0
.
2
1
6
4.
7
0
2
6
9
.
6
3
.
4
7
1
9
.
8
7
0
.
8
1
2
8
.
0
3
0
.
2
0
5
2
3
.
2
1
.
0
0
9
5
.
4
9
7
7
.
8
%
GW
A
-
7
D
G
r
o
u
n
d
w
a
t
e
r
4
/
2
5
/
2
0
1
6
0
0
5
1
.
2
0
.
8
3
9
3
0
.
0
8
5
0
0
1
0
6
2.
2
0
6
3
.
1
3
2
5
.
2
1
.
2
5
7
1
3
1
.
0
7
0
0
2
2
.
3
0
.
9
7
3
.
2
9
7
2
.
6
%
12
.
1
5
3
9
.
1
2
3
1
61
3
5
.
5
6
2
4
8
.
0
5
2
0
.
0
5
Charge Balance (%)
60
6
1
3
5
.
5
6
2
9
6
.
1
4
0
.
1
2
4
.
3
3
9
.
1
2
3
21
1
1
2
2
An
i
o
n
s
Cations
Al
k
a
l
i
n
i
t
y
,
C
O
3
A
l
k
a
l
i
n
i
t
y
,
H
C
O
3
C
h
l
o
r
i
d
e
Ni
t
r
o
g
e
n
,
N
O
2
pl
u
s
N
O
3
Su
l
f
a
t
e
Su
m
o
f
An
i
o
n
s
Ca
l
c
i
u
m
M
a
g
n
e
s
i
u
m
P
o
t
a
s
s
i
u
m
S
o
d
i
u
m
Sum of Cations 21
30
Pa
g
e
1 of
2
Dan River Steam Station CSA Supplement 2
Ta
b
l
e
3 ‐5:
Su
m
m
a
r
y
of
Ca
t
i
o
n
‐An
i
o
n
Ba
l
a
n
c
e
Di
f
f
e
r
e
n
c
e
s
Co
n
s
t
i
t
u
e
n
t
:
Mo
l
e
c
u
l
a
r
W
e
i
g
h
t
(
g
/
m
o
l
)
Ch
a
r
g
e
Eq
u
i
v
a
l
e
n
t
W
e
i
g
h
t
:
Si
t
e
L
o
c
a
t
i
o
n
M
a
t
r
i
x
D
a
t
e
Re
s
u
l
t
e
q
/
L
R
e
s
u
l
t
e
q
/
L
R
e
s
u
l
t
e
q
/
L
R
e
s
u
l
t
e
q
/
L
R
e
s
u
l
t
e
q
/
L
eq
/
L
R
e
s
u
l
t
e
q
/
L
R
e
s
u
l
t
e
q
/
L
R
e
s
u
l
t
e
q
/
L
R
e
s
u
l
t
e
q
/
L
e
q
/
L
Ri
v
e
r
b
e
n
d
12
.
1
5
3
9
.
1
2
3
1
61
3
5
.
5
6
2
4
8
.
0
5
2
0
.
0
5
Charge Balance (%)
60
6
1
3
5
.
5
6
2
9
6
.
1
4
0
.
1
2
4
.
3
3
9
.
1
2
3
21
1
1
2
2
An
i
o
n
s
Cations
Al
k
a
l
i
n
i
t
y
,
C
O
3
A
l
k
a
l
i
n
i
t
y
,
H
C
O
3
C
h
l
o
r
i
d
e
Ni
t
r
o
g
e
n
,
N
O
2
pl
u
s
N
O
3
Su
l
f
a
t
e
Su
m
o
f
An
i
o
n
s
Ca
l
c
i
u
m
M
a
g
n
e
s
i
u
m
P
o
t
a
s
s
i
u
m
S
o
d
i
u
m
Sum of Cations 21
30
GW
A
-
7
S
G
r
o
u
n
d
w
a
t
e
r
4
/
2
5
/
2
0
1
6
0
0
1
.
3
0
.
0
2
1
2
.
2
0
.
0
6
2
1
.
2
0
.
0
1
9
21
0
4
.
3
7
4
.
4
7
2
3
7
.
4
1
.
8
6
5
2
3
.
2
1
.
9
0
9
0
0
1
5
.
4
0
.
6
7
4
.
4
4
4
-
0
.
3
%
GW
A
-
8
D
G
r
o
u
n
d
w
a
t
e
r
4
/
2
5
/
2
0
1
6
0
0
1
4
2
2
.
3
2
8
3
.
9
0
.
1
1
0
0
3
8
8
8.
0
7
5
1
0
.
5
1
3
1
2
5
6
.
2
3
4
3
1
.
3
2
.
5
7
6
0
0
5
3
.
8
2
.
3
3
9
1
1
.
1
4
9
2
.
9
%
GW
A
-
8
S
G
r
o
u
n
d
w
a
t
e
r
4
/
2
5
/
2
0
1
6
0
0
7
5
.
3
1
.
2
3
4
5
.
7
0
.
1
6
1
0
.
0
2
6
0
17
6
3
.
6
6
3
5
.
0
5
8
2
7
.
2
1
.
3
5
7
2
0
1
.
6
4
6
0
0
5
5
.
1
2
.
3
9
6
5
.
3
9
9
3
.
3
%
GW
A
-
9
D
G
r
o
u
n
d
w
a
t
e
r
3
/
2
8
/
2
0
1
6
0
0
2
4
.
7
0
.
4
0
5
3
.
1
0
.
0
8
7
0
0
7
.
1
0
.1
4
8
0
.
6
4
6
.
7
9
0
.
3
3
9
1
.
9
8
0
.
1
6
3
0
0
4
.
8
9
0
.
2
1
3
0
.
7
1
5
5
.
5
%
GW
A
-
9
S
G
r
o
u
n
d
w
a
t
e
r
3
/
2
8
/
2
0
1
6
0
0
1
2
.
3
0
.
2
0
2
4
.
3
0
.
1
2
1
0
.
0
5
0
.
0
0
1
4
.
1
0
.0
8
5
0
.
4
0
9
1
.
0
5
0
.
0
5
2
0
.
5
3
7
0
.
0
4
4
3.25
0
.
0
8
3
7
.
1
5
0
.
3
1
1
0
.
4
9
9
.
0
%
MW
-
1
0
D
G
r
o
u
n
d
w
a
t
e
r
4
/
2
6
/
2
0
1
6
0
0
9
3
.
6
1
.
5
3
4
2
2
.
3
0
.
6
2
8
0
0
4
1
.
5
0
.8
6
4
3
.
0
2
6
3
3
.
8
1
.
6
8
6
1
0
.
6
0
.
8
7
2
0
0
1
7
.
3
0
.
7
5
2
3
.
3
1
4
.
5
%
MW
-
1
1
G
r
o
u
n
d
w
a
t
e
r
4
/
2
6
/
2
0
1
6
*
*
N
A
*
*
N
A
*
*
N
A
*
*
N
A
*
*
N
A
3
.
4
5
0
.
1
7
2
1
.
9
5
0
.
1
6
0
0
1
8
.
6
0
.
8
0
9
1
.
1
4
1
-
-
MW
-
1
1
D
G
r
o
u
n
d
w
a
t
e
r
4
/
2
5
/
2
0
1
6
0
0
1
2
0
1
.
9
6
7
2
4
.
9
0
.
7
0
1
0
.
2
0
.
0
0
3
7
6
.
8
1
.5
9
8
4
.
2
6
9
6
5
.
1
3
.
2
4
7
7
.
9
9
0
.
6
5
8
3
.
9
1
0
.
1
1
4
.
2
0
.
6
1
7
4
.
6
2
2
4
.
0
%
MW
-
1
2
G
r
o
u
n
d
w
a
t
e
r
4
/
2
5
/
2
0
1
6
0
0
8
.
6
0
.
1
4
1
4
.
9
0
.
1
3
8
0
0
8
.
4
0
.1
7
5
0
.
4
5
4
1
.
2
1
0
.
0
6
2
.
8
4
0
.
2
3
4
0
0
5
.
1
4
0
.
2
2
3
0
.
5
1
7
6
.
5
%
MW
-
1
2
D
G
r
o
u
n
d
w
a
t
e
r
4
/
2
5
/
2
0
1
6
0
0
7
5
1
.
2
3
9
.
8
0
.
2
7
6
0
0
2
9
0
.
6
0
4
2.
1
1
1
3
.
8
0
.
6
8
8
8
.
3
5
0
.
6
8
7
1
0
.
8
0
.
2
7
6
1
6
.
4
0
.
7
1
3
2
.
3
6
4
5
.
7
%
MW
-
2
2
B
R
G
r
o
u
n
d
w
a
t
e
r
4
/
2
5
/
2
0
1
6
0
0
1
1
4
1
.
86
9
1
8
.
8
0
.
5
3
0
0
4
2
.
1
0
.
8
7
6
3
.
2
7
5
0
00
0
0
0
0
0
0
-
100.0%
MW
-
2
3
B
R
G
r
o
u
n
d
w
a
t
e
r
3
/
2
9
/
2
0
1
6
0
0
2
1
7
3
.
5
5
7
4.
2
0
.
1
1
8
0
0
1
1
.
3
0
.
2
3
5
3
.
9
1
5
7
.
1
2
.
84
8
2
0
.
1
1
.
6
5
4
0
0
1
3
.
9
0
.
6
0
4
5
.
1
0
6
1
3
.
3
%
MW
-
2
3
D
G
r
o
u
n
d
w
a
t
e
r
3
/
2
9
/
2
0
1
6
0
0
2
3
.
1
0
.
3
7
9
2
.
7
0
.
0
7
6
0
0
2
0
.
3
0
.4
2
2
0
.
8
7
7
1
1
.
9
0
.
5
9
4
3
.
9
2
0
.
3
2
3
0
0
2
.
8
8
0
.
1
2
5
1
.
0
4
2
8
.
6
%
MW
-
3
0
8
B
R
G
r
o
u
n
d
w
a
t
e
r
4
/
2
5
/
2
0
1
6
0
0
1
1
4
1
.
8
6
9
1
3
.
7
0
.
3
8
6
0
0
8
1
1
1
6
.
87
8
1
9
.
1
3
3
5
4
.
5
2
.
7
1
8
9
.
7
6
0
.
8
0
3
0
0
4
.
5
2
0
.
1
9
7
3
.
7
1
8
-
6
7
.
5
%
MW
-
3
1
0
B
R
G
r
o
u
n
d
w
a
t
e
r
4
/
2
6
/
2
0
1
6
0
0
1
5
9
2
.
6
0
7
15
.
2
0
.
4
2
8
0
0
5
.
8
0
.
1
2
1
3
.
1
5
6
4
2
.
7
2
.
1
3
1
1
.
4
0
.
9
3
8
0
0
1
2
.
4
0
.
5
3
9
3
.
6
0
7
6
.
7
%
MW
-
3
1
1
B
R
G
r
o
u
n
d
w
a
t
e
r
4
/
2
6
/
2
0
1
6
0
0
1
9
2
3
.
1
4
8
23
.
7
0
.
6
6
8
0
0
4
6
.
9
0
.
9
7
6
4
.
7
9
2
6
0
.
1
2
.
9
9
8
12
.
2
1
.
0
0
4
3
8
.
8
0
.
9
9
2
2
5
1
.
0
8
7
6
.
0
8
1
1
1
.
9
%
MW
-
3
1
4
B
R
G
r
o
u
n
d
w
a
t
e
r
4
/
2
6
/
2
0
1
6
0
0
8
4
.
8
1
.
3
9
2
7
.
9
0
.
7
8
6
0
0
8
0
1
.
66
5
3
.
8
4
1
4
8
.
2
2
.
4
0
4
1
2
.
7
1
.
0
4
5
6
.
1
9
0
.
1
5
8
1
3
.
4
0
.
5
8
3
4
.
1
9
4
.
3
%
MW
-
3
1
5
B
R
G
r
o
u
n
d
w
a
t
e
r
4
/
2
6
/
2
0
1
6
0
0
1
5
8
2
.
5
9
3.
1
0
.
0
8
7
0
0
4
4
.
9
0
.
9
3
4
3
.
6
1
1
5
7
.
2
2
.
85
3
9
.
6
3
0
.
7
9
3
0
0
1
2
.
9
0
.
5
6
1
4
.
2
0
7
7
.
6
%
MW
-
3
1
7
B
R
G
r
o
u
n
d
w
a
t
e
r
4
/
2
6
/
2
0
1
6
1
9
2
6
.
4
9
6
.
8
1
.
58
7
5
.
6
0
.
1
5
8
0
0
1
2
.
1
0
.
2
5
2
8
.
3
9
7
7
8
.
6
3
.
9
2
0
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0
7
0
.
0
3
3
3
9
.
6
1
.
0
1
3
3
4
1
.
4
7
8
6
.
4
4
4
-
1
3
.
2
%
MW
-
3
1
8
D
G
r
o
u
n
d
w
a
t
e
r
4
/
2
6
/
2
0
1
6
0
0
5
5
.
2
0
.
9
0
5
8
.
1
0
.
2
2
8
0
0
1
0
3
2.
1
4
4
3
.
2
7
7
2
2
.
6
1
.
1
2
7
1
2
.
5
1
.
0
2
9
0
0
3
0
.
4
1
.
3
2
2
3
.
4
7
8
3
.
0
%
MW
-
9
D
G
r
o
u
n
d
w
a
t
e
r
4
/
2
6
/
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Pa
g
e
2 of
2
Dan River Steam Station CSA Supplement 2