Valley Sports Well
P-4
P-3
P-2
P-1
9-78
OW-3OW-2
AR-02
CLF-1
PT-10
MW-8A
LF-20DCLF-3B
CLF-2C
ML-3-1ML-1-1
MW-S27MW-S29
MW-S28
MW-S24
MW-S08
MW-S09
MW-S04
MW-S17
MW-S07
MW-S02
MW-S05
MW-S22
CLF-101
CLF-102
CLF-103
CLF-106
CLF-104
CLF-105
PT-04B1
GZW-6-1
PT-11B1P-2A
P-1A
MW-2P-3A
CLF-2B
CLF-3A
CLF-2A
MW-S23
MW-T24
CLF-107
GZW-9-2GZW-9-1
GZW-8-1
MW-SD27MW-SD29
MW-SD17
MW-SM13MW-SD13
GZW-11-1
ASBRV-D
ASBRV-U2
ASBRV-U1MW-BS04
MW-BS17
MW-BS13
MW-BS22
MW-BS01
MW-BS02
LF-18DBRLF-20DBR
GZW-11-2
LF-20SBRLF-18SBR
A'
B
B'
A
B-06 0.81 (2015)
OW-1 15.4 (2013)
MW-1 15.7 (2013)
J2-B1 1.16 (2013)
PT-09 1.85 (2015)
SW-101 0.18 (2015)
MW-S26 5.15 (2015)
MW-S32 1.82 (2015)
MW-SD37 4.3 (2015)
MW-S30 0.73 (2015)MW-S06 1.06 (2013)
MW-SD01 3.8 (2013)
MW-S15 1.19 (2015)
SW-102 0.212 (2015)
SW-103 0.234 (2015)
MW-S38 0.346 (2015)
MW-SD34 47.4 (2015)
LF-18D 8.40B (2015)
MW-S36 <0.147 (2015)
MW-S39 <0.147 (2015)
MW-S14 <0.156 (2015)
J2-B2 0.958 (2013)
MW-S01 9.31 (2013)
MW-S37 0.457 (2015)
MW-SD38 1.36 (2015)
MW-SD32 3.27 (2015)
PT-11B1 20.4 (2015)
PT-03B2 0.856 (2015)
MW-S35 <0.142 (2015)
PT-11B3 <0.15 (2013)
PT-11P <0.167 (2013)
MW-SD35 <0.142 (2015)
MW-SD39 <0.147 (2015)
MW-SD36 <0.150 (2015)
PT-11B2 <0.142 (2015)
GZW-7-2 39 (2012)
ML-1-3 10.9 (2013)
GZW-10-2 58 (2015)
MW-BS31 5.64 (2015)
MW-BS28 47.5 (2013)
GZW-8-2 0.199 (2015)MW-BS37 6.02 (2015)
MW-BS32 18.9 (2015)MW-BS34 2.53 (2015)
PT-03B1 5.64 (2015) MW-BM15 3.31 (2015)
MW-BM03 30.8 (2013)
MW-BS15 89.6 (2015)
MW-BS14 4.54 (2015)
MW-BS26 5.59 (2015)
MW-BS25 18.1 (2013)
MW-BS03 12.2 (2013)
MW-BS38 <0.142 (2015)
MW-BS39 <0.147 (2015)
MW-BS36 <0.150 (2015)
MW-BS35 <0.142 (2015)
J3-B1
MW-SD26 2.92 (2015)
MW-BS40 0.182 (2015)MW-SD40 42.3 (2015)MW-S40 0.468 (2015)
5
1
20
10
30
50
40
0.46
60
70 80
0.46
1
5
30
20
1
50
40
30
40
50
510
0.46
Q:\G
ISPr
ojects
\BR0
090-N
MISit
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ects\
Upda
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015\F
06_d
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_con
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BR_z
oom_
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7.mxd
DRAFT
Legend@A Monitoring Well
@A Monitoring Well (Destroyed)!( Surface Water Sample Location&% Active Public Water Supply Well&% Non-Active Public Water Supply Well
$B Assabet River Stage Elevation
Surface WaterWetlands1,4-Dioxane ISO ConcentrationContour in BedrockEstimated 1,4-Dioxane ISOConcentration Contour in BedrockCross Section A-A'
Cross Section B-B'0.57 (2015) 1,4-Dioxane Concentrations (µg/L) (Year Collected)
MW-S32
MW-BS32Overburden Monitoring Well
Bedrock Monitoring Well
Note:1. LF-18D and B-06 were sampled by Tetra Tech in August 2015. All other locations were sampled in November 2015 (except where noted)2. "<" indicates less than laboratory reporting limit.3. Only data from Overburden wells were used to draft contours. 0 100 20050
Feet
1,4-Dioxane Concentrations (µg/L) in BedrockGroundwater Most Recent Data Through
January 2016Nuclear Metals, Inc. Superfund Site
Concord, Massachusetts
Figure
6Acton, Massachusetts FEBRUARY 2016
de maximis, inc.
³
Service Layer Credits: Esri, HERE,DeLorme, MapmyIndia, ©OpenStreetMap contributors, andthe GIS user community
ASSABET 1A
MUNICIPAL
WELL
PT-03P, B2, B1
PT-09
PT-10
PT-11P, B3, B2, B1
MW-S15, BS, BM
OW-1
MW-1
MW-S06, SD
MW-S27,SD
MW-07,S
GZW-7-1, 7-2
HB-10,
10S
50
100
150
200
250
0
ELE
VA
TIO
N (F
EE
T N
GV
D)
0
100
150
200
250
ELE
VA
TIO
N (F
EE
T N
GV
D)
50
0
<0.16
3.27
<0.16
<0.16
<0.15
<0.16
0.79J
<0.16
<0.16
<0.167
1.0
4.7
1.0
<1.0
20.4
<1.0
2.0
<1.0
<1.0
<0.0708
124.33
124.49
<1.0
3.2
<1.0
<1.0
1.85
<0.5
<0.5
<0.5
<0.5
<2.0
MWS37,
SD, BS
124.66
<1.0
<1.0
<1.0
<1.0
2.53
1.4
6.7
4.0
<1.0
47.4
OVERBURDEN
TILL
BEDROCK
ASSABET
RIVER
NMI
AA'
500 1000 1500 2000 2500 3000
131.30
130.27
130.48
129.50
129.48
128.24
125.49
125.09
125.38
124.29
124.33
123.74
123.65
123.78
MW-SD34, BS
124.31
-25
MW-S40, SD, BS
124.26
124.33
124.53
EL. 123.53
MCLs ug/L
1,4-DIOXANE 0.46
ROD CLEANUP LEVELS
RISK BASED ug/L
VOCs and 1,4-Dioxane Distribution in
Cross-Section, Data through January 2016
DRAFT
Approximate Scale
Horizontal 1" = 250'
Vertical 1" = 50'
ACTON, MASSACHUSETTS
FIGURE
FEBRUARY 2016
7
NUCLEAR METALS SUPERFUND SITE
CONCORD, MASSACHUSETTS
MW-S36,SD,BS
PT-09
MW-SD34, BS
MW-S32,SD, BS
PT-11P, B3, B2, B1
LF-18D,
SBR,
DBR
CLF-107
CLF-3A, B
0
30
60
90
120
150
0
30
60
90
120
150
ELE
VA
TIO
N (F
EE
T N
GV
D)
ELE
VA
TIO
N (F
EE
T N
GV
D)
ASSABET
RIVER
ASSABET RIVER
SOUTHWEST NORTHEAST
B B'
PT-10
OVERBURDEN
TILL
BEDROCK
124.54
123.66
124.72
126.41
123.59
124.17
124.66
124.44
124.66
124.31
124.29
124.33
124.49
124.42
124.91
124.91
<1.0
<1.0
<1.0
<1.0
<0.0735
<1.0
2.0
<1.0
<1.0
<0.075
<1.0
1.0
<1.0
<1.0
<0.075
<1.0
3.2
<1.0
<1.0
1.85
<1.0
8.6
2.8
5.0
1.82
<1.0
1.1
<1.0
<1.0
3.27
<1.0
2.1
1.5
<1.0
18.9
8.40 B
<0.5
<0.5
<0.5
<0.5
<2.0
<0.16
3.27
<0.16
<0.16
<0.15
<0.16
0.79J
<0.16
<0.16
<0.167
=1.0
4.7
1.0
<1.0
20.4
<1.0
<1.0
<1.0
<1.0
2.53
1.4
6.7
4.0
<1.0
47.4
124.91
MCLs ug/L
1,4-DIOXANE 0.46
0 300 600 900 1200 1500 1800
<1.0
2.0
<1.0
<1.0
<0.0708
2.0
MW-S40,SD,BS
<1.0
<1.0
<1.0
<1.0
0.468
3.2
15
5.9
6.0
42.3
<1.0
<1.0
<1.0
<1.0
0.182
124.26
124.33
124.53
EL. 122.0
EL. 123.53
ROD CLEANUP LEVELS
RISK BASED ug/L
VOCs and 1,4-Dioxane Distribution in
Cross-Section, Data through January 2016
DRAFT
Approximate Scale
Horizontal 1" = 150'
Vertical 1" = 30'
ACTON, MASSACHUSETTS
FIGURE
FEBRUARY 2016
8
NUCLEAR METALS SUPERFUND SITE
CONCORD, MASSACHUSETTS