39-060 Atwood Drive wireless tower siteEnvironm.entalSafetyHealthGeotechnical
T
O'Reilly, Talbot & Okun 4VTMTMVrab 293 Bridge Street
[ A S S O C I A T E S] -
Suite 500 ~
II
Springfield, MA 01103
Tel 413 788 6222
Fax 413 788 8830
Email office@oto-env.com
D
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November 3, 1999
File No. J84-05-17
Mr. Peter McErlain
Office of Planning and Development
City Hall
210 Main Street
Northampton, MA 01060
Re: Limited Removal Action
Atwood Drive
Northampton, MA
Dear Mr. McErlain:
This letter documents completion of a Limited Removal Action (LRA) as defined in the Massachusetts
Contingency Plan (310 CMR 40.0318) to remove lead contaminated soil from the above referenced
property in Northampton, Massachusetts. Our report is subject to the limitations 'attached in
Appendix A.
Background
A site locus and site plan are provided as Figures 1 and 2 respectively. An environmental site
assessment performed by O'Reilly, Talbot & Okun Associates, Inc. (OTO) for a perspective leasee
indicated that fill material was likely present on the Atwood Drive property. A series of test pits was
performed on the property, which included analytical testing of the fill material. The fill material was
tested for Extractable Petroleum Hydrocarbons (EPH), polychlorinated byphenols (PCBs) and RCRA
8 metals. Location Test Pit .1 (TP-1) contained approximately 2.5 feet of granular fill with
concentrations of lead at 347 mg/kg, above the applicable Reportable Concentration (RCS-1) for total
lead of 300 mg/kg. No EPH or PCB compounds were detected above Reportable Concentrations. A
copy of the test pit log for TP-1 is provided in Appendix B. Analytical data are summarized in Table 1
and analytical data sheets are provided in Appendix C. We understand that the City of Northampton
was notified of concentrations of lead in site soil above reportable concentrations by facsimile letter
dated February 3, 1999
Additional Fill Characterization
The extent of, lead impacted soil around TP-1 was further characterized through a boring program
performed December 18, 1998 and January 29, 1999. Ten additional soil samples were collected on
these dates and analyzed for total lead. The results are summarized in Table 1. The locations of
samples (NOHO-2,3,5,7,8,9,101,103,105, and 108) and results of total lead analyses are shown on
Figure 2. Each of these samples was collected from the fill material within 2.0 to 2.5 feet of the ground
surface, with the exception of NOHO-9, which was collected from the natural soil material
underlying the fill. Soil sample NOHO-5 had the highest total lead concentration at 783 mg/kg. The
T
O'Reilly, Talbot & Olcun
[ A S _S 0 C- I_A T _.E. S ] i - _
OHO-5 sample was tested for leachable lead by the Toxicity Characteristic Leaching Procedure
N
(TCLP) and found to contain a leachable lead concentration of 6.07 mg/1, which exceeded the 5.0 mg/l
standard defining a characteristically hazardous waste.
Based on the analytical data, an area of lead contaminated soil of approximately 20 cubic yards was
identified as shown on Figure 2.
n Groundwater Characterization
In addition to fill characterization, a groundwater monitoring well (NOHO-1) was installed adjacent
to test pit TP-1 (approximately 15 feet south in the inferred downgradient groundwater flow direction)
to evaluate potential groundwater impacts. The well was installed on December 18, 1999 in a boring
drilled to a depth of 24 feet. The monitoring well installation and subsurface conditions encountered
are shown on the boring log attached in Appendix B.
Soil samples were collected by split spoon using standard penetration tests continuously to depths of
15 feet and screened for VOCs with the PID: No VOCs were detected. Soil conditions consisted of
granular fill to a depth of 2 feet, followed by fine to medium sand, with trace amounts of silt. Thin (1
to 2 inch thick) layers of clay were observed below 10 feet. Groundwater was encountered at a depth
of approximately 18 feet.
a On December 28, 1998 a groundwater sample was collected from the monitoring well. The groundwa-
ter sample was collected using an individually dedicated disposable plastic bailer. Prior to sample
a collection three to five times the volume of standing water in the well was removed to provide a
sample of formation water in the well for collection. Groundwater samples were than collected into
pre-preserved bottles for analysis for Extractable and Volatile Petroleum Hydrocarbons (EPH/VPH)
j Volatile Organic Compounds (VOCs) and dissolved lead. The dissolved lead sample was filtered prior
u to preservation to remove sediment. The analytical data sheets for the groundwater analyses are also
attached in Appendix C. As shown, no contaminants were detected in the groundwater samples.
A groundwater sample was also screened in the field for pH and specific conductance. The pH reading
was 6.5 and the specific conductance reading was 290. These values are within the range typical for this
geographic region.
Limited Removal Action Excavation
The lead contaminated soils were excavated by CT Environmental, Inc. of Longmeadow,
Massachusetts on May 27, 1999. The excavation was observed by Bruce H. Nickelsen of O'Reilly,
Talbot & Okun Associates, Inc. The soils were excavated to a depth of 2.5 feet (the depth of fill) and
to the lateral limits shown on Figure 2. Excavated soils were placed on top of and covered with plastic
sheeting. Approximately 5 cubic yards was excavated from the vicinity of the NOHO-5 sample
location, which had been found to be characteristically hazardous based on TCLP testing. The
remaining approximately 15 cubic yards of soil were excavated and stockpiled separately. A soil sample
was collected from the 15 cubic yard pile (STOCK-1) and analyzed for TCLP lead. A concentration of
n 3.23 mg/l of leachable lead'was detected from this sample, indicating the 15 cubic yards pile of soil was
J not a characteristically hazardous waste.
Page 2
i I
~J O'Reilly, Talbot & Okun
A S S 0_ Z- I - A T _E S - 1 - - -
Soil Disposal
On September 9, 1999, the 15 cubic yard stockpile was transported to the Northampton Landfill for
use as daily cover under 'a Massachusetts Bill of Lading. The Bill of Lading is attached-in Appendix D.
The 5 cubic yard pile was transported to Chem-Met Services, Inc. of Brownstown, Michigan for
disposal in their hazardous waste landfill. A copy of the hazardous waste manifest showing this
disposal is attached in Appendix D. Both Bill of Lading and hazardous waste manifest were signed by a
representative of the City of Northampton as generator of the waste material.
L Conclusions
Based on the investigations and analytical test results described in this letter, lead impacted soil has
been removed from the vicinity of the TP-1 location to levels below applicable Reportable
Concentrations. Given that soils which exceed applicable reportable concentrations have been
removed, no further actions are warranted under the MCP, other then maintenance of this
documentation report for a period of five years as required under 310 CMR 40.0318. You should sign
lJ section M of the last page of the original Bill Of Lading, and keep it with your records. ,
lJ It has been our pleasure to work with you on this project. Please feel free to call us if you have any
questions or comments.
Very truly yours,
O'Reilly, Talbot & Okun Associates, Inc.
'y
Bruce H. Nickelsen Kevin J. Reilly
Associate Principal
cc Wayne Feiden
Attachments: Figures
Tables
Appendix A - Limitation
Appendix B - Test Pit/Boring Logs
Appendix C - Analytical Data
Appendix D - Bill of Lading, Manifest
u Page 3
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Atwood Drive
Northampton, Massachusetts
Site Locus
October 1999
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*NOHO-1
LIMITED REMOVAL
ACTION EXCAVATION
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A T W O O D D R I V E
LEG ND:
FARMLAND
- • • - PROPERTY LINE
SAMPLE LOCATION
-d~- MONITORING WELL LOCATION
(163) TOTAL LEAD CONCENTRATIONS
APPROXIMATE SCALEi V = 10'
NOHO-8
(159) +
SOIL DISPOSED
OF AS HAZARDOUS
NOHO_; WASTE
10.9)
NOHO-5
(783)1: 4- Ai
NOHO-9;=-;ih NON -103
(73.4):'.•`.;:2 (10.
NOHp-7 6
:.a;::' (347):':.:::•3 NOHO-3
NOH13-101 (69)
(69.0) L
TNOHO-105
V (9,26)
J j
SOIL DISPOSED J
AT LANDFILL + f
NOHO-2
(163)
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_L - [ A S S 0 C-I A - T E S
T
4-- 41CCMIEMMW
LIMITATIONS
1. The observations presented in this report were made under the conditions
described herein. The conclusions presented in this report were based solely upon
the services described in the report and not on scientific tasks or procedures
beyond the scope of the project or the time and budgetary constraints imposed by
the client.
U 2. In preparing the report O'Reilly, Talbot, Okun & Associates, Inc. relied on
certain information provided by state and local officials and other- parties
a referenced herein, and on information contained in the files of state or local
regulatory agencies. Although there may have been some degree of overlap in the
information provided by these sources, O'Reilly, Talbot, Okun & Associates, Inc.
did not attempt to independently verify the accuracy or completeness of all
information reviewed or received during the course of this assessment.
3. Observations were made of the site and of the structures on the site as indicated
within the report. Where access to portions of the 'site or to structures on the site
was unavailable or limited, we render no opinion as to the presence or hazardous.
materials or oil, or to the presence of indirect information relating to hazardous
materials or oil in that portion of the site. In addition, we render no opinion as to
the presence. of hazardous materials or oil, where direct observations of portions
a of the site where obstructed by objects or coverings on or over these surfaces.
.4. Unless otherwise specified in the Report, we did not perform testing or analyses
to determine the presence or concentration or concentration- of asbestos or
polychlorinated biphenyls (PCBs) at the site or in the environment at the site.
a 5. The purpose of this Report was to assess the physical characteristics of the subject
site with respect to the presence of oil or hazardous material (OHM) in soil or
groundwater at the site, and to assess risks associated with detected OHM, within
the meaning of the Massachusetts Contingency Plan, 310 CMR. 40.0000. No
specific attempt was made to check on the compliance of present or past owners
..or operators of the site with federal, state, or local laws and regulations,
environmental or otherwise.
6. Risk assessment was performed in accordance with generally accepted practices of
r government agencies and other consultants conducting similar characterizations.
u The findings of the risk characterization are dependent on numerous assumptions
and uncertainties inherent in the risk assessment process. Therefore, the findings
rl of the risk assessment should not be interpreted as an absolute characterization of
actual risks, but as general indicators highlighting potential sources of risk at the
site. Although the range of uncertainty in the risk characterization has not (and
j~ cannot) be quantified, the use of conservative assumptions throughout the process
D
D
would be expected to err on the side of protection of human health and the
L '
environment.
D
7. Where analytical data or information regarding site environmental conditions was
unavailable or limited, we render no opinion as to risks due to. oil or hazardous
D
materials in those portions of the site, or to oil or hazardous materials not tested
for
.
8. Our report was prepared for the exclusive benefit of our client. Reliance upon
D
the report and its conclusions is not extended to third parties or future property
.owners. We acknowledge copies of our report may be submitted to DEP for
D
MCP compliance purposes.
D
.
D
D.
_
D
D
D
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O'Reilly, Talbot & Okun Associates, Inc.
-PROJECT
Test Pit No. TP-1
293 Bridge Street, Suite 500
Description: Atwood Drive
Job No. 084-5-17
Springfield, Massachusetts. 01103
Location: Northhampton, MA
Date: 06/23/98
(413)-788-6222
Engineer/Geologist: Bruce Nickelsen Contractor: Gary Guertin Ex. Ground Elev:
Weather: Overcast, 70's Backhoe: Case 580 Start: 9:10
Capacity: 1/2 yard cubic yard Finish: 9:30
EXCAV.
BOULDER
PID
DEPTH
SOIL DESCRIPTION
EFFORT
COUNT
REMARKS
Brown Fine to Medium sand with some brick fragments.(Fill)
1
E
None
S-1 =ND
2.5'
Sample S-1 collected from 0-2.5 feet
None
E'
5
Natural Brown Fine-Sand, trace silt.
S-2, collected from 8'
S-2 = ND
8.0 End of Exploration
10
.
REMARKS:
1. Samples screened with TEI 580B Photoionization detecto r, referenced to parts per million(PPM) benzene in air.
2. Soil at 8' was moist.
PLAN ;LEGEND EFFORT
E = Easy
M = Moderate
i D = Difficult
Vol. _
r-,
OWEILLY, TALBOT & OKUNASSOCIATES, INC.
ENVIRONMENTAL AND GEOTECHNICAL ENGINEERING CONSULTANTS
LOG OF BORING
NOHO -1
SHEET 1 OF 1
PROJECT Atwood Drive
LOCATION Northhampton
PROJECT NO. 84-05-17
DRILLING CONTRACTOR Seaboard
FOREMAN Jeff N.
DATE STARTED
DATE FINISHED
12/18198
12/18/98
DRILLING EQUIPMENT B-53
COMPLETION DEPTH
GROUND SURFACE ELEV.
24.0
DATUM
TYPE BIT H.S.A.
SIZE &TYPE OF CORE BARREL
NO. SAW. 7 DIST. UNDIST.
CASING 3"
TIME
FIRST
COWL.
HR.
CASING HAMM.
WEIGHT DROP
WATER LEVEL (FTJ
SAMPLER 21/4" Split Spoon
BORING North 17 feet South of TP-I
SAMPLER
WEIGHT 140 pound
DROP
LOCATION
HAMMER
30 inches
ENGINEER/GEOLOGIST Melissa Schumacher
SAMPLES
SAMPLES
DEPTH
PENETR.
REC.
TYPE/
DESCRIPTION
FIELD
SOIL
REMARKS
FT.
RESIST.
IN.
NO.
MEASUREMENTS
DESCRIPTION
BL/6IN.
4/5/6/8
20"
S-1
Medium, dense, brown, fine to medium SAND, trace silt, brick fragments.
ND
Fill
7/8/618
6"
S-2
Medium, dense, brown, fine to medium SAND, trace medium, dense,
ND
2.0
brown, silt and trace fine gravel.
Fine
to
Medium
6/7/6/11
12"
S-3
Medium, dense, brown, fine to medium SAND, trace medium, dense,
ND
Sand
5
brown, silt and trace fine gravel.
10/9/7/7
12"
S4
Medium, dense, brown, fine to medium SAND, little, medium dense,
ND
brown, coarse SAND, trace silt, (moist).
10/12/16118
18"
S-5
Medium, dense, brown, fine to medium SAND, little, medium, dense,
ND
brown, coarse SAND, trace silt, (moist).
10
16/14/18/11
18"
S-6
Dense, brown, fine to medium SAND, trace dense brown SILT wet
ND
at 18.5.
Bottom 2" wet, dense, brown, silty fine SAND. -
9/7/9111
20"
S-7
Top 0.5 feet Medium, dense, little SILTY, fine SAND, (moist).
ND
(Watertasble 12.511)
Bottom 1.5" Medium, dense, dark brown, silty, fine SAND, (saturated)
Little, very stiff, dark brown, clay.
15
20
F
25
F
Remarks:
1. Samples screened infield using TEI Model 580B referenced to PPM of Benzene in air. Readings in meter units."N.D." indicates none detected 4
2. Well set at 24', 10' of 2" PVC screening (24.0'-14.0'), I2' of filter sand (240-120- 10.0'- Ground Surface) 2' of bentonite (120-10.0'), PVC rising pipe 10' -N2 feet above ground surface, metal rising pi e
(N 2 ft below ground surface to N 211 above ground surface).
I
I~
SPECTI4UNI ANALI'TiCAL, INC.
Massachusetts Certification MA 138
L- Connecticut Approval No. PH 0777
New Hampshire ID No. 2538
New York ID No. 11393
Florida HRS87448
O'ReiUy, Talbot & Okun'.Assoc. July 9, 1998
293 Bzidge Street
L Springfield, MA 01103
Attn: Bruce Nickelsen
a Client Project No.: 784-0520 Location: Atwood Drive - Northampton, MA
Lab ID No. Client ID
AB10787 TP-1/S-1
Analysis Requeste
Extractable 011
d
Hydrocarbons
Modified SW846
808118082
To tal Arseni c
To tal Bari um
Total Cadmium
Total Chromi um
To tal Lead
n
Total Mercury
To to 1 Sel eni um
LJ
Total Silver
AB10788 TP-41S-1
Extractable 011
Hydrocarbons
n
Modified SW846 •
8081/8082
Total Arsenic
To tal Bari um
Total Ca dmi um
Total Chromi um
Total Lead
To tat Mercury
Total Setenlum
To tal S11 ver
D
AB10789 TP-5/S-1
Extractable 011.
Hydrocarbons
Modified SW846
808118082
Total Arsenic
Total Bari um
Total Cadmium
Total Chromiurh
Total Lead
Total Mercury
Continued next page
i
ENVIRONMENTAL ANALYSES
- - - - - 1 l Almgren Drive --Agawam-) Massachusetts 01001- -413=789=9018 FAX-413=789-4076 - - - - -
SPECTRUM ANALYTICAL, INC.
Laboratory Report
Client ID: TP-I/S-1 Location: Atwood Drive - Northampton, MA
Lab ID No: ABI0787 Client Job No: J84-0520
Matrix: Soil Preservative: Refrigeration
Collected: 06/23/98 by OTO Container: 1 Glass Soil Jar
Received on 07/02/98 by DDR Condition of Sample as Received: Satisfactory
QC and Data Review by Delivered by: Courier
I~
LJ
n Parameter
PCB-1016
PCB-1221
PCB-1232
~J PCB-1242
u PCB-1248
PCB-1254.
a PCB-1260
nn Decachlorobiphenyl
% ~J
Solids,
~J
i
Polychlorinated Biphenyls (PCB's)
Modified SW846 8081/8082
Result (ug/Kg)
MI)L
Extracted
Analyzed
Analyst
Not detected
250
07/02/98
07/06/98
TO
Not detected
250
07/02/98
07/06/98
TO
Not detected
250
07/02/98
07/06/98
TG
Not detected
250
07/02/98
07/06/98
TO
Not detected
250
07/02/98
07/06/98
TO
750
250
07/02/98
07/06/98
TG
Not detected
250
07/02/98
07/06/98
TG
.73
07/02/98
07/06/98
TG
91.3
0.1
07/02/98
07/02/98
SEC
SPECTRUM ANALY TICAL, INC.
Laboratory Report
Client ID: TP-1/S-1 Location: Atwood Drive - Northampton, MA
Lab ID No.: AB10787 Client Job No.: J84-0520
Matrix: Soil Preservative: Refri eration
Collected: 06/23/98 by OTO Container: 1 Glass Soil Jar
Received on 07/02/98 by DDR Condition of Sample as Received: Satisfactory
QC and Data Review by Delivered by: Courier
Extractable Petroleum Hydrocarbons
MA DEP Modified EPA 8270/8100
Parameter for AB10787 Results
Aliphatics/Aromatics (mg/Kg)
C9 - C18 Aliphatics
Not detected
C19- C36 Aliphatics
Not detected
C11- C22 Aromatics
Not detected
Targeted PAH's Analytes (ug/Kg)
Acenaphthene
Not detected
Acenaphthylene
Not detected
Anthracene
Not detected
Benzo (a) anthracene
Not detected
Benzo (b) fluoranthene
Not detected
Benzo (k) fluoranthene
Not detected
Benzo (a) pyrene
Not detected
Benzo (g,h.i) perylene
Not detected
Chrysene
Not detected
Dlbenz (a,h) anthracene
Not detected
Fluoranthene
Not detected
Fluorene
Not detected
Indeno (1,2,3-cd) pyrene
Not detected
2-Methylnaphthalene
Not detected
Naphthalene
Not detected
Phenanthrene
Not detected
Pyrene
Not detected
Surrogate Recovery(%)
1-Chloro-octadecane(%SR) 43
Ortho-Terphenyl(%SR) 42
% Solids 91.3
AIDL
Extracted Analyzed Analyst
33
07/02/98
07/08/98
MB
33
07/02/98
07/08/98
MB
33
07/02/98
07/08/98
MB
148.0
07/02/98
07/08/98
MB
148.0
07/02/98
07/08/98
MB
148.0
07/02/98
07/08/98
MB
148.0
07/02/98
07/08/98
MB
148.0
07/02/98
07/08/98
MB
148.0
07/02/98
07/08/98
MB
148.0
07/02/98
07/08/98
MB
148.0
07/02/98
07/08/98
MB
148.0
07/02/98
07/08/98
MB
148.0
07/02/98
07/08/98
MB
148.0
07/02/98
07/08/98
MB
148.0
07/02/98
07/08/98
MB
148.0
07/02/98
07/08/98
MB
148.0
07/02/98
07/08/98
MB
148.0
07/02/98
07/08/98
MB
148.0
07/02/98
07/08/98
MB
148.0
07/02/98
07/08/98
MB
07/02/98
07/08/98
MB
07/02/98
07/08/98
MB
0.1
07/02/98 07/02/98 . SEC
I
SPECTRUM ANALYTICAL, INC.
Laboratory Report
Client ID: TP-1/S-1
Location:
Atwood Drive - Northampton, MA
Lab ID No: AB10787
Client Job No: J84-0520
n
Matrix: Soil
Preservative: Refrigeration
1 Gl
i1 J
i
Collected: 06/23/98 by OTO
DDR
98 b
02
7
ass S0
ar
Conta
ner:
le as Received: Satisfactor
Condition of Sam
y
/
Received on 0
/
p
y
QC and Data Review by
Delivered by: Courier
Metals
Parameter Result (mg/Kg)
MDL
Method
Digested
Analyzed
. Analyst
Total Arsenic nd
0.904
EPA 200.7
07/08/98
07/08/98
CR
Total Barium 51.3
0.904
EPA 200.7
07/08/98
07/08/98.
CR
Total Cadmium nd
0.904
EPA 200.7
07/08%98
07/08/98
CR
Total Chromium 13.8
Total Lead 347.,
0.904
0.452
EPA 200.7
EPA 200.7
07/08/98
07/08/98
07108/98
07/08/98
CR
CR
Total Mercury nd
0.225
EPA 245.1
07/08/98
07/07/98
JM
Total Selenium nd
0.452
EPA 200.7
07/08/98
07/07/98
CR
Total Silver nd
1.81
EPA 200.7
07/08/98
07/07/98
CR
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CHAIN -T-- RECORD
I,
Page of SPECTRUM ANALYTICAL
kOJECT NO.: REPORTTO:
F-o ITE NAME: /zt '77
I` OCATION: STATES ~a ADDRESS:
-9EFERENCE QUOTE NUMBER (RQN): CITY STATE ZIP
IDURCHASE ORDER NO.: INVOICETO:
PROJECT Mgr:f1
3AMPLER(s):
CITY STATE ZIP
SAMPLE TYPE & MATRIX CODES:
C
ONT
AIN
ERS
VO
C's
SVO
C's
T
PH
METALS
O
THER
1
^I = 40C 2 = HCI 3 = H2SO4 4 = HNO3 5 = OTHER
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SPECIAL INSTRUCTIONS: SPECIAL HANDLING' Please El 4
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~I~, r~ ' •a 1± ~;a iryl I ,i~~i,;fj_1~ ❑ Dispose of Sample after 60 days
Standard TAT - 7 to 10 Business days j
61& ❑ Special TAT-24 hr-48 hr-72hr-5b. days '
:TAT begins when sample is received attest facility.
~ . Y ,,/y 1~';.~' bN. 2. ! Y • TAT for samples reed after 3 pm will begin on the next business day.
• Ail TAT s are subject to laboratory approval and customer consent. f
❑ Fax results when available to
) DATE RESULTS NEEDED:
11 Almgren Drive -Agawam, Massachusetts 01001 0 413-789-9018 • Fax 413-789-4076 I
SPECTRUM ANALYTICAL, DIC,
Massachusetts Certification MA 138
Connecticut Approval No. PH 0777
New Hampshire ID No. 2538
New York ID No. 11393
Florida HRS87448
O'Reilly, Talbot & Okun Assoc..
293 Bridge Street
Springfield, MA 01103
Attn: Bruce Nickelsen
Client Project No.: J0840517
Tab ID No.
AB29056
AB29057
AB29058
AB29059
AB29060
AB29061
Client ID
NOHO-2
NOHO-5
NOHO-3
NOHO- 7
NOHO-9
NOHO-10
AB29062
AB290 63
AB290 64
AB29065
AB29066
AB29067
AB29068
NOHO-11
NOHO-12
NOHO-13A
NOHO-13B
NOHO-14
NOHO-15
NOHO-16
December 30, 1998
Location: Atman - Northampton
lvsi
Total Lead
Total Lead
Total Lead
Total Lead
Total Lead
Total Lead
Extractable Oil Hydrocarbons
Modified SW846.8082
Total Lead
Extractable Oil Hydrocarbons
Modified SW846 8082
Total Leach
Extractable Oil Flydrocarbons
Modified SW846 8082
Total Lead
Extractable Oil Hydrocarbons
Modified SW846`8082
Total Lead
Extractable Oil Hydrocarbons
Modified SW846 8082
Total Lead
Extractable Oil Hydrocarbons
Modified SW846 8082
Total. Lead
Extractable Oil Hydrocarbons
Modified SW846 8082
Total Lead
Extractable Oil Hydrocarbons
Continued next page .
ENVIRONMENTAL ANALYSES
- - 11 AlmgresDrive- Agawam;-Massachusetts-01001--• 413-789-9018 FAX-413-7894070
Lab TD No. Client ID
AB290 68 1vOHO-16
AB290 69 NOHO-l 7
a
AB290 70 NOHO-l 8
II
Analysis Requested
Modified SW846 8082
Total Lead
Extractable Oil Hydrocarbons
Modified SW846 8082
Total Lead
Extractable Oil Hydrocarbons
Modified SW846 8082
uth rized y
ani1 ayeh v
ENVIRONMENTAL ANALYSES Preside t ry Director f
HAImgren-D-rive •-Agawam; Massachusetts-01001---413-789-901-8-•--Fi1X413-789-4076 - - - -
SPECTRUM ANALYTICAL, I NC.
Laboratory Report I
Client ID: NOHO-2 Location: Atman - Northampton
Lab ID No: AB29056 Client Job No: J0840517
Matrix: Soil Preservative: Refrigeration
Collected: 12/18/98 by OTO Container: 1 Clear Glass Jar
Received on 12/21/98 by MBR Condition of Sample as Received: Satisfactory
QC and Data Review by Delivered by: Client
I
Total Lead
n EPA Method 6010/200.7
Parameter result (mg/Kg) XML
Digested Analyzed Analyst
Total Lead 163 0.449 12/29/98 12/30/98 DMM
lJ
i
SPECTRUM ANALYTICA., INC.
Laboratory Report
Client ID: NOHO-3
Lab ID No: AB29058
Matrix: Soil
Collected: 12/18/98 by OTO
Received on 12/21/98 by MBR
QC and Data Review by
l_l
Location: Atrnan - Northampton
Client Job No: J0840517
Preservative: Refrigeration
Container: 1 Clear Glass Jar
Condition of Sample as Received: Satisfactory
Delivered by: Client
Total Lead
n EPA Method 6010/200.7
L
n Parameter Result (mg/Kg)
u
NII)L
Digested Analyzed Analyst
0.464 12/29/98. 12/30/98 DMM
SPECTRUM ANALYTICAL, INC.
Laboratory Report
Client ID: NOHO-5 Location: Atman - Northampton
Lab ID No: AB29057 Client Job No: J0840517
Matrix: Soil Preservative: Refrigeration
Collected: 12/18/98 by OTO Container: 1 Clear Glass Jar
Received on 12/21/98 by MBR Condition of Sample as Received: Satisfactory
n QC and Data Review by Delivered by: Client
L-.l
-J Total Lead
EPA Method 6010/200.7
Parameter Result (mg/Kg) MDL
Digested
Total Lead 783 0.455 12/29/98
Analyzed
12/30/98
Analyst
DMM
SPECTRUM ANALYTICAL, INC.
Laboratory Report
F1
Client ID: NOHO-7
Lab ID No: AP29059
Matrix: Soil
Collected: 12/18%98 by OTO
Received on 12/21/98 by MBR
~l
QC and Data Review by
Location: Ataman - Northampton
Client Job No: J0840517
Preservative: Refrigeration
Container: 1 Clear Glass Jar
Condition of Sample as Received: Satisfactory
Delivered by: Client
Total Lead
EPA Method 6010/200.7
n Parameter Result (mg/Kg) MDL
0.558
Digested
12/29/98
Analyzed Analyst
12/30/98 DMM
SPECTRUM ANALYTICAL
INC. r
,
Laboratory Report
D
Client ID: N®H- ®-9
I
Location: Atman -Northampton
Lab ID No: AB29060 Client Job No: J0840517
Matrix: Soil
Preservative: Refrigeration
J
Collected: 12/18/98 by
OTO Container: 1 Clear Glass Jar
Received on 12/21/98 b
y MBR Condition of Sample as Received: Satisfactory
QC and Data Review by
Delivered by: Client
D
Total Lead
EPA Method 6010/200.7
Parameter
r
Result (mg/Kg) M DL
Digested Analyzed Analyst
D
Total Lead
.
47.2 0.458 12/29/98 12/30/98 DMM
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SPECTRUIVI,ANALYTICAL, C.
i Massachusetts Certification M-MA 138
Connecticut Approval # PH 0777
Rhode Island # 98 & Maine # n/a
n New Hampshire ID # 2538
New York ID #11393
Florida HRS87448
~ O'Reilly, Talbot & Okun Assoc. January 11, 1999
L_] 293 Bridge Street
Springfield, MA 01103
Attn: Bruce Xickelsen
L_.J
Client Project No.: J840517 Location: Atwood Drive
LJ
Lab ID No. Client ID An ysis Requested
AB29697 1VOHO-1 EPA Method 8260
Extractable Oil Hydrocarbons
Soluble Lead
volatile Petroleum Hydrocarbons
~I AB29698 1VOHO-l0. volatile Petroleum Hydrocarbons
U EPA Method 8260
Extractable Oil Hydrocarbons
Soluble Lead
Ell
If
V
Director
I
ENVIRONMENTAL ANALYSES
i
- 11 Alzngren Drive Agawati,-MassachusettsOl001 = 41-3=789-9018 • -FAX 413=789-4076-- - - - - - -
E
0
L
L~
SPECTRUM ANALYTICAL, INC.
Laboratory Report
Client ID: N0H0-1
Lab ID No: AB29697
Matrix: Ground Water
Sampled on12/28/98 by OTO
Received on 12/28/98 by MBR
QC and Data Review by AM
Parameter for AB29697
Location: Atwood Drive
Client Job No.: J340517
Preservative: Refrigeration, HCl
Container : 2 VOA Vials
Condition of Sample as Received: Satisfactory
Delivered by: Client
Volatile Organics
EPA Method 8260
Result (ug/L) N ML
Analyzed Analyst
Benzene
Not detected
1.0
01/09/99
SN
Bromobenzene
Not detected
1.0
01/09/99
SN
Bromochloromethane
Not detected
1.0
01/09/99
SN
Bromodichloromethane
Not detected
1.0
01/09/99
SN
Bromoform
Not detected
1.0
01/09/99
SN
Bromomethane
Not detected
1.0
01/09/99
SN
n-Butylbenzene
Not detected
1.0
01/09/99
SN
sec-Butylbenzene
Not detected
1.0
01/09/99
SN
tert-Butylbenzene
Not detected
1.0
01/09/99
SN
Carbon tetrachloride
Not detected
1.0
01/09/99
SN
Chlorobenzene
Not detected
1.0
01/09/99
SN
Chloroethane
Not detected
1.0
01/09/99
SN
Chloroform
Not detected
1.0
.01/09/99
SN
Chloromethane
Not detected
1.0
01/09/99
SN
2-Chlorotoluene
Not detected
1.0
01/09/99
Sri
4-Chlorotoluene
Not detected
1.0
01/09/99
SN
1,2-Dibromo-3-chloropropane
Not detected
1.0
01/09/99
SN
Dibromochloromethane
Not detected
1.0
01/09/99
SN
1,27Dibromoethane (EDB)
Not detected
.1.0
01109/99
SN
Dibromomethane
Not detected
1.0
01/09/99
SN
1,2-Dichlotobenzene
Not detected
1.0
01/09/99
SN
1,3-Dichlorobenzene
Not detected
1.0
01/09/99
SN
1,4-Dichlorobenzene
Not detected
1.0
01/09/99
SN
Dichlorodifluoromethane
Not detected
1.0
01/09/99
SN
1,1-Dichloroethane
Not detected
1.0
01/09/99
SN
1,2-Dichloroethane
Not detected
1.6
01/09/99
SN
1,1-Dichloroethene
Not detected
1.0
01/09/99
SN
cis-1,2-Dichloroethene
Not detected
1.0
01/09/99
SN
trans-1,2-Dichloroethene
Not detected
1.0
01/09/99
SN
1,2-Dichloropropane
Not detected
1.0
01/09/99
SN
1,3-Dichloropropane
Not detected
1.0.
01/09/99
SN
2,2-Dichloropropane Not detected 1.0 01/09/99 SN
01/09/99 SN
1,1-Dichloropropene Not detected 1.0
cis-1,3-Dichloropropene Not detected 1.0 01/09/99 SN
Continued next page - - - - - - - -
r
Volatile Organics
EPA Method 8260
Parameter for AB29697
Result (ug/L)
M DL
Analyzed
Analyst
trans-1,3-Dichloropropene
Not,detected
1.0
01/09/99
sN
Ethylbenzene
Not detected
2.0
01/09/99
SN
Hexachlorobutadiene
Not detected
1.0
01/09/99
SN
Isopropylbenzene
Not detected
1.0
01/09/99
SN
4-Isopropyltoluene
Not detected
1.0
01/09/99
SN
Methylene chloride
Not detected
1.0
01/09/99
sN
Naphthalene
Not detected
4.0
01/09/99
SN
n-Propylbenzene
Not detected
1.0
01/09/99
SN
Styrene
Not detected
1.0
01/09/99
SN
1,1,1,2-Tetrachloroethane
Not detected
1.0.
01/09/99
SN
1,1,2,2-Tetrachloroethane
Not detected
1.0
01/09/99
SN
Tetrachloroethene
Not detected
8.0
01/09/99
sN
Toluene
Not detected
3.0
01/09/99
SN
1,2,3-Trichlorobenzene
Not detected
1.0
01/09/99
SN
1,2,4-Trichlorobenzene
Not detected
1.0
01/09/99
SN
1,1,1-Trichloroethane
Not detected
1.0
01/09/99
SN
1,1,2-Trichloroetharie
Not detected
1.0
01/09/99
SN
Trichloroethene
Not detected
1.0
01/09/99
SN
Trichlorofluoromethane
Not detected
1.0
01/09/99
SN
1,2,3-Trichloropropane
Not detected
1.0
01/09/99
SN
1,2,4-Trimethylbenzene
Not detected
4.6
01/09/99
SN
1,3,5-Trimethylbenzene
Not detected
2.0
01/09/99
SN
m,p-Xylenes
Not detected
2.0
01/09/99
SN
o-Xylene
Not detected
.1.0
01/09/99
SN
Vinyl chloride
Not detected
1.0
01/09/99
SN
Methyl-t-butyl ether
Not detected
2.0
01/09/99
SN
BFB Surrogate Recovery
99
01109/99
SN
p-DFB Surrogate Recovery
103
01/09/99
SN
CLB-d5 Surrogate Recovery
97
01/09/99
SN
Parameter for AB29697
Aliphatics/Aromatics (mg(L)
C5-C8 Aliphatic Hydrocarbons
C9-C12 Aliphatic Hydrocarbons
C9-C10.Aromatic Hydrocarbons
Unadjusted C5-C8 Aliphatics
Unadjusted C9-C12 Aliphatics
n _
Client ID: NOHO-A
: AB29697
b ID No
L
l
.
a
Matrix: Ground Water
l
Collected: 12/28/98by o'ro
Target VPH Analytes (ug/L)
Benzene
Ethylbenzene
Methyl-tert-butylether
Naphthalene
Toluene
M,p-Xylenes '
o-Xylene
Received: 12/28/98by MBR
Volatile Petroleum Hydrocarbons
MADEP VPH 97-12
11
I J
H
Dilution Factors
Carbon Chain Dilution Factor
Target Analytes Dilution Factor
Location:. Atwood Drive
Client Job No.: J840517
Preservative: Refrigeration, HCl
Container: 2 VOA Vials
Condition of Sample as Received: See Attached Sheet
Results
MDL
Analyzed
Analyst
Not detected
0.150
01/09/99
SN
Not detected
0.050
01/09/99
SN
Not detected
0.050
01/09/99
SN
Not detected
0.150
01/09/99
SN
Not detected
0.050
01/09/99
ISN
Not detected
5.0
01/09/99
SN
Not detected
5.0
01/09/99
SN
Not detected
5.0
01/09/99
SN
Not detected
. 5.0
01/09/99
SN
Not detected
5.0
01/09/99
SN
Not detected
5.0
01/09/99
SN
Not detected
5.0
01/09/99
SN
1
01/09/99
SN
1
01/09/99
SN
NA
01/09/99
SN
NA
01/09/99
SN
118
01/09/99
SN
106
01/09/99
SN
Surrogate Recoveries
2,5-Dibromotoluene PID (%SR)
2,5-Dibromotoluene FID (%SR)
2,5-Dibromotoluene GCMS (%SR).
4-Bromofluorobenzene GCMS (%SR)
D
i
i_
Were all QA/QC procedures required bythe VPH method followed? Yes No
Were all performance/acceptance standards for required QA/QC procedures achieved? Yes -C No
Were any significant modifications made to the VPH method, as specified in Section 11.3? Yes*
* If yes is answered to above question, then this sample was run via GCMS using all VPH method specified QC criteria.
I attest
the ma
SPECTRUM ANALYTICAL, INC.
Laboratory Report
of those individuals immediately responsible for obtaining the information,
:k-ij, to the best of my knowledge and belief, accurate and complete.
01/11/99
SPECTRUM ANALYTICAL, INC.
Client ID: NOHO-1 Location: Atwood Drive
I Lab ID No.: AB29697 Client Job No.: J840517
Matrix: Ground Water Preservative: Refrigeration/HN03
Collected: 12/28/98by OTO Container: 1 Amber / 1 Plastic
Received: 12/28/98by MBR Condition of Sample as Received: See Attached Sheet
Extractable Petroleum Hydrocarbons
n
MADEP EPH 98-1, SW846 3510C Separatory Funnel Liquid-Liquid Extraction
Parameter forAB296.97
L
Results
lAIDL
Extracted
Analyzed
Analyst
)
Aliphatics/Aromatics (mg/
C9-C18 Aliphatic Hydrocarbons
Not detected
0.2
12/30/98
01/03/99
KS
C19-C36 Aliphatic Hydrocarbons
Not detected
0.2
12/30/98.
01/03/99
KS
C11-C22 Aromatic Hydrocarbons
Not detected
0.2
12/30/98
01/03/99
KS
Unadjusted C11-C22 Aromatics
Not detected
0.2
12/30/98
01/03/99
KS
j
LJ
Diesel PAH Analytes (ug/L)
Naphthalene
Not detected
10.0
12/30/98
01/03/99
KS
.2-Methylnaphthalene
Not detected
10.0
12/30/98
01/03/99
KS
Phenanthrene
Not detected
10.0
12/30/98
01/03/99
KS
a
Acenaphthene
Not detected
10.0
12/30/98
01/03/99
KS
Other Target PAR Analytes (ug/L)
Acenaphthylene
Not detected
10.0
12/30/98
01/03/99
KS
u
u
Anthracene
Not detected.
10.0
12/30/98
01/03/99
KS
Benzo (a) anthracene
Not detected
10.0
12/30/98
01/03/99
KS
Benzo (a) pyrene
Not detected
10.0
12/30/98
01/03/99
KS
Benzo (b) fluoranthene
Not detected
10.0
.12/30/98
01/03/99
KS
Benzo (g,h,i) perylene
Not detected
10.0.
12/30/98
01/03/99
KS
Benzo (k) fluoranthene
Not detected
10.0
12/30/98
01/03/99
KS
Chrysene -
Not detected
10.0
12/30/98
01/03/99
KS
Dibenzo (a,h) anthracene
Not detected
10.0
12/30/98
01/03/99
KS
LJ
~l
Fluoranthene
Not detected
10.0
12/30/98
01/03/99
KS
Fluorene
Not detected
10.0
12/30/98
01/03/99
KS
Indeno (1,2,3-cd) pyrene
Not detected
10.0
12/30/98
01/03/99
KS
Pyrene
Not detected
10.0
12/30/98
01/03/99
KS
J
Dilution Factors
Carbon Chain Dilution Factor
1
12/30/98
01/03/99
KS
l
Target Analyte Dilution Factor
1
12/30/98
01/03/99
KS
Parameter forA B29697
Results AML Extracted Analyzed Analyst
Surrogate Recoveries
1-Chloro-octadecane Aliphatic (%SR) 82
Ortho-Terphenyl Aromatic (%SR) 62
2-Bromonaphthalene Fractionation (%SR) 43
2-Fluorobiphenyl Fractionation (%SR) 51
12/30/98
01/03/99
KS
12/30/98
01/03/99
KS
12/30/98
01/03/99
KS
12/30/98
01/03/99
KS
J
Were all QA/QC procedures required by the EPH method followed? Yeses No
Were all performance/acceptance standards for required QA/QC procedures achieved? Yes C-, No
Were any significant modifications made to the EPH method, as specified in Section 11.3? Yes*-C_,-No
* If yes answered to above question, the aromatic hydrocarbons from C11- C22 along with target PAH analytes were performed
via GC/MS following all EPH method specified QC criteria.
I attest that based upf n m inquiry -of those individuals immediately responsible for obtaining the information,
J the materi cont ' d in' s repo is to the best of my knowledge and belief, accurate and complete.
01/11/99 l
Pres en b to Director I
- -
i
i
SPECTRUM ANALYTICAL, INC.
l J Laboratory Report
Client ID: NOHO-1 Location: Atwood Drive
' Lab ID No: AB29697 Client Job No: J840517
i J Coll cted Ground 28/98at by OTO Container: 1 Amb g/ 1 Plastic
Received on 12/28/98 by MBR Condition of Sample as Received: Satisfactory
n QC and Data Review by Delivered by: Client
U
Soluble Lead
EPA Method 200.7
Result (mg/L) MDL
nd 0.005
Extracted Analyzed Analyst
01/04/99 01/06/99 DMM
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SPECTRUM ANALY71CAL, VC,
massachusetts certif=don M-MA 133
` Connecticut Approval # PH 0979
Rhodo Island *199 & Maine nAa
Igcw Hampshirc ID # 2533
flew York ID # 11393
J Florida. X97448
®'Rciffy, Talbot & Okun Assoc. .February 3, 1.999
293 Bddsc Street .
U Spzingffcld, MA 01103
Arm: Brucc Xickelsezz
J Client Project No.: 30840537 Location-, At=an -Northampton
TCLP Zeatd
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ENVIRONMENTii,i+ AMALYSES
_ _ii_Almen~~av~ Agawa~a, hiassacbusetts0i001 413-789-X618 ° FA~4f3 799-076
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SPECTRUM ANALYTICAL, INC.
Laboratory Report (Subcontracted Analysis)
Chew M: NOHO-S
Lab ID No: AB29057
1Nlatria: Snail
~Ilei1: 12118/98 by e3T0
Rec6vedon12/2119$ by MBR
CSC and Data R.-miew by AM
Parameter
Location: At=aa - Northampton
Client Job No: J0840517
Preservative, Refri eration
Container: 1 Cleat lass Jar
Condition of Saffipie as Received: Satisf=ory
]Delivered icy: Cent
TCLP Lead
EPA Method 1311/5W846 6010
Result (M) iL
UP
0010
n TCLF Lead
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02/01/99 02103/99 CR
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Spectrum Analytical, Inc,
Laborstory Rep®rt Supplement
Re ereaise
Methods for the Detgimination of Organic Cornpouuds in Drinking Water. EPA-60014-381039. EMSL 1983.
Methods for Chemical Analysis 6f Water aridVastes. EPA 60014-79-020. EMI SL 1983_
Methods for Organic Chemical Analysis of Municipal and Industrial Wastewater. EPA 60014-92-057. EMSL 19'91
Test Methods for Evaluating Solid Waste. Physical/Chernical Methods. ]EPA SW-846. 1986.
standard Methods for the Exam? matinon of Water and Wastes. APRA-AWWA-V4PCP• 16ih- Edidon. 1935.
Standard Methods for Comparison of waterborne: Petroleum Oils by Gas Chromatography. ASTM D 3323. 1982.
Oil Spill Identification System. U-$. Coast Guard CG-13-52-77. 1977.
Handbook for Analytical Quality Control in Water and Wastewater Laboratories. EPA 600/4-79-019_ EMSL 1979.
Choosing Cast-Effective QAtQC (Quality Assurance/Quality Control) Programs for Chemical Anslyses. EPA 600/4-35/056.
EMSL 1955.
Re rt Notations
Not Detected,
- The compound Was not detected at a concentration equal to or above
Not Det, ND or nd,
the established method detection limit.
NC
= Mot Calculated
MCI:.
.
= EPA maximum Contamination Level
VOA
= VolratileOrganic Analysis
BFB
_ 4-Bromofluorobeneene
(Ara EPA 624 ,Saarrogate)
(Ara EPA 624 Surrogate)
p_-pFB
= 1,4-Difluorobenzene
= L:hlorobenzene-d5
(Art EPA 624 Surrogate)
CLIP-d5
gCp
2-Promo-1=chloropropeane
(An EPA 601 Surrogate)
T
= a,a,a-Trifluororoluene
(An EPA 602 Surrogate)
Decachlorobiphenyl
- (an EPA 60818080 Surrogate)
Defini ns
Surrogate Recovery The recovery (expressed as a percent) of a non-method analyte (see surrogates listed
above) added to the sample for the purpose of monitoring system performance.
Matrix Spike Recovery e The recovery (expressed as a percent) of method analyses added to the sample for the
purpose of determining any effect of sample composition on analyte recovery.
Laboratory Replicate = Two, sample aliquots taken in the analytical laboratory and analyzed separately with.
identical procedures. Analyses of laboratory duplicates give a measure of the preceision associated with
laboratory procedures, but not with sample collection, preservation, or storage procedures.
d
ntifical circumstances measure
Field Duplicate = Two separate samples collected at the same time and place
treated exactly the same throughout field and laboratory procedures. Analysis of Field P gag
of the precision associated with sample collection, preservaton and storage.. as well as with laboratory procedures.
Relative Percent Difference RFD) = The precision measurement obtained on duplicate/replicate analyses.
%RPD is calculated as: ooPPD va.-lu-e ,+ue2-3lO1000/6
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Mamaohuwtts Cortifieation M-MA 131
Cosnwticbat Approval # PH 0777
Rhode Island # 98 & Maine a n/a
14ow Hampshire ID 2539
New York M ##11393
Florida HRS87448
O'Reilly, Taalbof & ®kun Assoc. January S, 15999
295 1 zidgs: ,S'imvi .
S,,zsdngfield, MA 01193
Attn: Bruce Nickelson
Client Project No.: 30840517 Location: Atwood
AB29860 NOHO-8
Wiabo 'r Presiarce,
ENS'IRONKFN7AL ANALYSES
I1 AlmgnnUriec ^ Agawam,Aiassacfiusefisi}TOiiT-~ 413=789=90f8-°-FfiX-41:3'=7tsiJ=40'tb-
TO' d .200* ON TS: VT 66, SO u*et :-131
I
SPECTRUM ANALYTIC.,, INC.
Laboratory Report
Client ID: NOM-8
Lab III No: 29860
Matrix: Soil
1
Collected: 12118/98 by OTO
Received on 12/31 j98 by MMBR
QC and Data Review by
L_1
Location: Atwood
Cheidt Job No: JUS40517
Preservative: Refrigeration
Container: 1 Clear Glass Jar
Condition of Sample as Received: Satisfactory
Delivered by: Client
Total Lead
EPA Method 50101200.7
Parameter Result (mom)
Total bead 159
LJ
u
J
ZO' d 200 * oN ZS:17T 66, SO uet
MUL
0.470
Digested Analyzed Analyst
01/04/98 0.1/05/99 DMM
f
:-131
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Spectrum Anslydcal, Inc.
Laboratory Report Saapplea'eaat
Methods for the Determination of Organic Compounds in Drinking Water. EPA-600/4-1351039. EMSL 1988.
!Methods for Chemical Analysis of Water and Wastes. FPA 60014-79-020. EMSL 1953.
Methods for Organic Chemical Analysis of Municipal and Industrial Wastewater. EPA 64014.82-057. EMSL 19112.
qL
Test Methods for Evaluating Solid Waste. PhysicaliChermical Methods. EPA SW 546. 1956.
Standard Methods for the Examinatinon of Water and Wastes. APIA-AWWA-WPCF. 16th Edition_ 1935.
Standard Methods for Comparison of Waterborne Petroleum Oils by Gas Chromatography. ASTM D 3328. 1982.
~J Oil Spill Identification System. U.S. Coast Guard CCs-D-52-77. 1977.
Handbook for Analytical Quality Control in `'Mater and Wastewater Laboratories- EPA 60014.79-019. EMSL 1979.
a Choosing Cost Effective QA/QC (Quality Assura=JQuality Control) Programs for Chemical Analyses. EPA 60014-351056.
EMSL 1985.
n ~nrt Notations
Ll Not Detected, = The compound was not defected at a concentration equal to or above
Not Det, ND or nd the established method detection limit.
NC Nos Calculated
MCL EPA 1bl=imum Contamination Level
VOA = Volatile Organic Analysis
13F33 m 4-Br°omofluorobenzene (An EPA 624 Surrogate)
p-DFl3 1,4,Diffuorobenzene (An EPA 624 Surrogate)
CLB-d5 = Chlorobenzene-dS (An .SPA. 624 Surrogate)
I~ 13CP _ 2-.Eromo-l-chloropropane (An EPA 601 Surrogate)
u TFT a ga-Tri uarotoluene (An EPA 602 Surrogate)
Decachlerobiphenyl = (an EPA 60818080 Surrogate)
Surrogate Recover, = The recovery (expressed as a percent) of a non-method analyte (see surrogates listed
J above) added to the sample for the purpose of monitoring system performance.
Matrix Spike Recovery The recovery (expressed as a percent) of method analytes added to the sample for the
purpose of determining any effect of sample composition on analyte recovery.
Laboratory Replicate = Two sample aliquots taken. in the analytical laboratory and analyzed separately with
J identical procedures. Analyses of laboratory duplicates give a measure of the precession associated with
laboratory procedures, but not with sample collection, preservation, or storage procedures.
Field Duplicate _ Two separate samples collected at the same time and place under identifrcal circumstances and
J treated exactly the same throughout Reid and laboratory procedures. Analysis of Field duplicates give a measure
of the precision associated with sample collection, prcgervaton and storage, as well as with laboratory procedures.
Relative Percent Difference IUD) =The precision measurement obtained on duplicate/replicate anatlyses.
J
%RPD is calculated as:
%R]?D Umlmcl -uhL 0 300%
ave. value -
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SPECTRUM ANALYTICAL, INC.
Massachusetts Certification M-MA 138
Connecticut Approval # PH 0777
Rhode Island 98 & Maine # n/a
New Hampshire ID # 2538
LJI
New York ID # 11393
Florida HRS87448
O'Reilly, Talbot & Okun Assoc.
L_1
293 Bridge Street
Springfield, MA 01103
Attn: Bruce Nickelsen
Client Project No.: J084 Location: Atwood
Lab ID No.
Client ID
AB32346
NOHO-101
AB32348
NOHO-103
-
AB32350
NOHO-105
AB32353
NOHO-108
AB32356
NOHO-11
[U-1
AB32390
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NOHOCOMP
Analysis Rec
Total Lead
Total Lead
Total Lead
Total Lead
February 3, 1999
Conductance
.
'EPA Method
8260
TPH by GC
EPA Method
8270
Conductance
EPA Method
8260
TPH by GC
EPA Method
8270
tho ed b
aniba ` h
Preside L a or Director
ENVIRONMENTAL ANALYSES
-
i~ - - -11 Almgren Drive Agawam, Massachusetts` 01001 -4-1-3489=9018 • TAX-413=789-4076-
SPECTRUM ANALYTICAL, INC.
Laboratory Report
Client ID: NOHO-101 Location: Atwood
Lab ID No: AB32346 Client Job No: J084
l_l Matrix: Soil Preservative: Refrigeration
Collected: 01/29/99 by OTO Container: 1 Clear Glass Jar.
Received on 01/29/99 by MBR Condition of Sample as Received: Satisfactory
QC and Data Review by Delivered by: Client
lJ
n
L 1
7
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Parameter
Total Lead
D
~J
H
n
n
~l
i F-1 U .
IJ
Total Lead
EPA Method 6010/200.7
Result (mg/Kg) MDL
Digested Analyzed Analyst
69.9 0.454 02/02/99 02/03/99 CR
r~ SPECTRUM ANALYTICAL, INC.
Laboratory Report
n
Client ID: NOHO-103 Location: Atwood
Lab ID No: AB32348 Client Job No: J084
I__ 1 Matrix: Soil Preservative: Refrigeration
Collected: 01/29/99 by OTO Container: 1 Clear Glass Jar
Received on 01/29/99 by MBR Condition of Sample as Received: Satisfactory
QC and Data Review by Delivered by: Client
l_
L1
-1 Parameter
u Total Lead
L~
I
L
L~
u
Total Lead
EPA Method 6010/200.7
Result (mg/Kg) XML
10.2 0.454
Digested Analyzed Analyst
02/02/99 02/03/99 CR
SPECTRUM ANALYTICAL, INC.
Laboratory Report
~J Client ID: NOHO-105 Location: Atwood.
Lab ID No: AB32350 Client Job No: J084
L ..l Matrix: Soil Preservative: Refrigeration
Collected: 01/29/99 by OTO Container: 1 Clear Glass Jar
Received on 01/29/99 by MBR Condition of Sample as Received: Satisfactory
n QC and Data Review by Delivered by: Client
SPECTRUM ANALYTICAL, INC.
J Laboratory Report
n
l Client ID: NOHO-108 Location: Atwood
n Lab ID No: AP32353 Client Job No: J084
`---I Matrix: Soil Preservative: Refrigeration
Collected: 01/29/99 by OTO Container: 1 Clear Glass Jar
Received on 01/29/99 by MBR Condition of Sample as Received: Satisfactory
QC and Data Review by Delivered by: Client
l1
l~
1 Parameter
Total Lead
LJ
J
Total Lead
EPA Method 6010/200.7
Result (mg/Kg) MDL
Digested Analyzed
10.9 0.447 02/02/99 02/03/99
Analyst
CR
n SPECTRUM ANALYTICAL, INC.
Laboratory Report
J Client ID: NOHO-11 Location: Atwood
Lab ID No.. AB32356 Client Job No.: J084
Matrix: Soil
Collected: 01/29/99 b OTO
Received on 01/29/99 by NOR
QC and Data Review by
Preservative: Refrigeration
Container : 3 Clear Glass Jars
Condition of Sample as Received: Satisfactory
Delivered by: Client
Semivolatile Organics
EPA Method 8270
Parameter for AB32356
Result (ug/Kg)
MDL
Extracted
Analyzed
Analyst
Acenaphthene
Not detected
151.0
02/02/99
02/03/99
KS
Acenaphthylene
Not detected
151.0
02/02/99
02/03/99
KS
Anthracene
Not detected
151.0
02/02/99
.02/03/99
KS
Benzidine
Not detected
151.0
02/02/99
02/03/99
KS
Benzoic acid
Not detected
755.0
02/02/99
02/03/99
KS
Benzo (a) athracene
Not detected
151.0
02/02/99
02/03/99
KS
Benzo (b) fluoranthene ,
Not detected
151.0
02/02/99
02/03/99
KS
Benzo (k) fluoranthene
Not detected
151.0
02/02/99
02/03/99
KS
Benzo (g,h,i) perylene
Not detected
151.0
02/02/99
02/03/99
KS
Benzo (a) pyrene
Not detected
151.0
02/02/99
02/03/99
KS
Benzyl alcohol
Not detected
302.0
02/02/99
02/03/99
KS
Bis (2-chloroethoxy) methane
Not detected
151.0
02/02/99
02/03/99
KS
Bis (2-chloroethyl) ether
Not detected
151.0
02/02/99
02/03/99
KS
Bis (2-chloroisopropyl) ether
Not detected
151.0
02/02/99
02/03/99
KS
Bis (2-ethylhexyl) phthalate
Not detected
1510.0
02/02/99
02/03/99
KS
4-Bromophenyl phenyl ether
Not detected
151.0
02/02/99
02/03/99
KS
Butyl benzyl phthalate
Not detected
151.0
02/02/99
02/03/99
KS
4-Chloroaniline
Not detected
302.0
02/02/99
02/03/99
KS
2-Chloronaphthalene
Not detected
151.0
02/02/99
02/03/99
KS
4-Chloro-3-methylphenol
Not detected
302.0,
02/02/99
02/03/99
KS
2-Chlorophenol
Not detected
151.0
02/02/99
02/03/99
KS
4-Chlorophenyl phenyl ether
Not detected
151.0
02/02/99
02/03/99
KS
Chrysene
Not detected
151.0
02/02/99
02/03/99
KS
Dibenz (a,h) anthracene
Not detected
151.0
02/02/99
02/03/99
KS
Dibenzofuran
Not detected
151.0
02/02/99
02/03/99
KS
Di-n-butylphthalate
Not detected
151.0
02/02/99
02/03/99
KS
1,3-Dichlorobenzene
Not detected
151.0
02/02/99
02/03/99
KS
1,4-Dichlorobenzene
Not detected
151.0
02/02/99
02/03/99
KS
1,2-Dichlorobenzene
Not detected
151.0
02/02/99
02/03/99
KS
3,3'-Dichlorobenzidine
Not detected
302.0
02/02/99
02/03/99
KS
Continued next page..
Parameter for AB32356
Result (ugWg)
MDI. .
Extracted.
Analyzed
Analyst.
2,4-Dichlorophenol
Not detected
151.0
02/02/99
02/03/99
KS
2,6-Dichlorophenol
Not detected
151.0
02/02/99
02/03/99
KS
Diethyl phthalate
Not detected
151.0
02/02/99
02/03/99
KS
2,4-Dimethlylphenol
Not detected
151.0
02/02/99
02/03/99
KS
4,6-Dinitro-2-methylphenol
Not detected
755.0
02/02/99
02/03/99
KS
2,4-Dinitrophenol
Not detected
755.0
02/02/99
02/03/99
KS
2,4-Dinitrotoluene
Not detected
151.0
02/02/99
02/03/99
KS
2,6-Dinitrotoluene
Not detected
151.0
02/02/99
02/03/99
KS
1,2-Diphenylhydrazine
Not detected
151.0
02/02/99
02/03/99
KS
Di-n-Propylnitrosoamine
Not detected
151.0
02/02/99
02/03/99
KS
Fluoranthene
Not detected
151.0
02/02/99
02/03/99
KS
Fluorene
Not detected
151.0
02/02/99
02/03/99
KS
Hexachlorobenzene
Not detected
151.0
02/02/99
02/03/99
KS
Hexachlorobutadiene
Not detected
151.0
02/02/99
02/03/99
KS
Hexachlorocyclopentadiene
Not detected
151.0
02/02/99
02/03/99
KS
Hexachloroethane
Not detected
151.0
02/02/99
02/03/99
KS
Indeno (1,2,3-cd) pyrene
Not detected
151.0
02/02/99
02/03/99
KS
Isophorone
Not detected
151.0
02/02/99
02/03/99
KS
2-Methylnaphthalene
Not detected
151.0
02/02/99
02/03/99
KS
2-Methylphenol (0-cresol)
Not detected
151.0
02/02/99
02/03/99
KS
4-Methylphenol (p-cresol)
Not detected
151.0
02/02/99
02/03/99
KS
Naphthalene
Not detected
151.0
02/02/99
02/03/99
KS
2-Nitroaniline
Not detected
755.0
02/02/99
02/03/99
KS
3-Nitroaniline
Not detected
755.0
02/02/99
02/03/99
KS
4-Nitroaniline
Not detected
755.0
02/02/99
02/03/99
KS
Nitrobenzene
Not detected
151.0
02/02/99
02/03/99
KS
2-Nitrophenol
Not detected
151.0
02/02/99
02/03/99
KS
4-Nitrophenol
Not detected
755.0
02/02/99
02/03/99
KS
N-Nitrosodimethylamine
Not detected
151.0
02/02/99
02/03/99
KS
N-Nitrosodiphenylamine
Not detected
151.0
02/02/99
02/03/99
KS
Pentachlorophenol
Not detected
755.0
02/02/99
02/03/99
KS
Phenanthrene
Not detected
151.0
02/02/99
02/03/99
KS
Phenol
Not detected
151.0
02/02/99
02/03/99
KS
Pyrene
Not detected
302.0
02/02/99
.02/03/99
KS
1,2,4-Trichlorobenzene
Not detected
151.0
02/02/99
02/03/99
KS
2,4,5-Trichlorophenol
Not detected
151.0
02/02/99
02/03/99
KS
2,4,6-Trichlorophenol
Not detected
151.0
02/02/99
02/03/99
KS
Pyridine
Not detected
151.0
02/02/99
02/03/99
KS
Dimethyl phthalate
Not detected
151.0
02/02/99
02/03/99
KS
Di-n-octyl phthalate
Not detected
151.0
02/02/99
02/03/99
KS
n SPECTRUM ANALYTICAL, INC.
Laboratory Report
Client ID: NOHO-11 Location: Atwood
Lab ID No.: AB32356 Client'Job No.: J084
Matrix: Soil
Collected: 01/29/99 by OTO
Received on 01/29/99 by MBR
n QC and Data Review by
Preservative: Refrigeration
Container: 1 Clear Glass Jar
Condition of Sample as Received:
Delivered by: Client
Satisfactory
Volatile Organics
EPA Method 8260
Parameter for AB32356
Result (ug/Kg)
MDL
Extracted
Analyzed
Analyst
Benzene
Not detected
31.8
02/02/99
02/02/99
CD
Bromobenzene
Not detected
31.8
02/02/99
02/02/99
CD
Bromochloromethane
Not detected
31.8
02/02/99
02/02/99
CD
Bromodichloromethane
Not detected
31.8
02/02/99
02/02/99
CD
Bromoform
Not detected
31.8
02/02/99
02/02/99
CD
n-Butylbenzene
Not detected
31.8
02/02/99
02/02/99
CD
sec-Butylbenzene
Not detected
31.8
02/02/99
02/02/99
CD
tert-Butylbenzene
Not detected
31.8
02/02/99
02/02/99
CD
Carbon tetrachloride
Not detected
31.8
02/02/99
02/02/99
CD
Chlorobenzene
Not detected
.31.8
02/02/99
02/02/99
CD
Chloroform
Not detected
31.8
02/02/99
02/02/99
CD
2-Chlorotoluene
Not detected
31.8
02/02/99
02/02/99
CD
4-Chlorotoluene
Not detected
31.8
02/02/99
02/02/99
CD
1,2-Dibromo-3-chloropropane
Not detected
31.8
02/02/99
02/02/99
CD
Dibromochloromethane
Not detected
31.8
02/02/99
02%02/99
CD
1,2-Dibromoethane (EDB)
Not detected
31.8
02/02/99
02/02/99
CD
Dibromomethane
Not detected
31.8
02/02/99
02/02/99
CD
1,2-Dichlorobenzene
Not detected
31.8
02/02/99
02/02/99
CD
1,3-Dichlorobenzene
Not detected
31.8
02/02/99
02/02/99
CD
1,4-Dichlorobenzene
Not detected
31.8
02/02/99
02/02/99
CD
1,1-Dichloroethane
Not detected
31.8
02/02/99
02/02/99
CD
1,2-Dichloroethane
Not detected
31.8
02/02/99
02/02/99
CD
1,1-Dichloroethene
Not detected
31.8
02/02/99
02/02/99
CD
cis- 1,2-Dichloroethene
Not detected
31.8
02/02/99
02/02/99
CD
trans-1,2-Dichloroethene
Not detected
31.8
02/02/99
02/02/99
CD
1,2-Dichloropropane
Not detected `
31.8
02/02/99
02/02/99
CD
1,3-Dichloropropane
Not detected
31.8
02/02/99
02/02/99
CD
2,2-Dichloropropane
Not detected
31.8
02/02/99
02/02/99
CD
-l
Continued next page..
Parameter for AB32356
result (ug/Kg)
MDL
Extracted
Analyzed
'
Analyst
n
l
1,1-Dichloro ro ene
P p
Di
hl
i
Not detected
N
t d
t
t
d
31,8
31
8
02/02/99
02/02/99
CD
~l
oropropene
c
c
s-1,3-
e
ec
e
o
.
02/02/99
02/02/99
CD
trans-1,3-Dichloropropene
Not detected
31.8
02/02/99
02/02/99
CD
Ethylbenzene
Not detected
31.8
02/02/99
02/02/99
CD
Hexachlorobutadiene
Not detected
63.6
02/02/99
02/02/99
CD
n
Isopropylbenzene
Not detected
31.8
02/02/99
02/02/99
CD
4-Isopropyltoluene
Not detected
31.8
02/02/99
02/02/99
CD
Methylene chloride
l
h
h
Not detected
t
N
t d
t
d
31.8
63
6
02/02/99
02/02/99
CD
ene
t
a
Nap
ec
e
e
o
.
02/02/99
02/02/99
CD
n-Propylbenzene
Not detected
31.8
02/02/99
02/02/99
CD
Styrene
Not detected
31.8
02/02/99
02/02/99
CD
1,1,1,2-Tetrachloroethane
Not detected
31.8
02/02/99
02/02/99
CD
n
1,1,2,2-Tetrachloroethane
Not detected
31.8
02/02/99
02/02/99
CD
l J
Tetrachloroethene
Not detected
31.8
02/02/99
02/02/99
CD
Toluene
z
b
Not detected
N
d
t
t
d
31.8
63
6
02/02/99
02/02/99
CD
en
ene
1,2,3-Trichloro
e
ec
e
ot
.
02/02/99
02/02/99
CD
1,2,4-Trichlorobenzene
Not detected
63.6
02/02/99
02/02/99
CD
1,1,1-Trichloroethane
Not detected
31.8
02/02/99
02/02/99
CD
1,1,2-Trichloroethane
Not detected
31.8
02/02/99
02/02/99
CD
Trichloroethene
Not detected
31.8
02/02/99
02/02/99
CD
Trichlorofluoromethane
Not detected
31.8
02/02/99
02/02/99
CD
a
1,2,3-Trichloropropane
h
lb
Not detected
d
N
d
t
t
. 31.8
31
8
02/02/99
02/02/99
CD
enzene
y
1,2,4-Trimet
ot
e
ec
e
.
02/02/99
02/02/99
CD
1,3,5-Trimethylbenzene
Not detected
31.8
02/02/99
02/02/99
CD
m,p-Xylenes
Not detected
63.6
02/02/99
02/02/99
CD
o-Xylene
Not detected
31.8
02/02/99
02/02/99
CD
Methyl-t-butyl ether
Not detected
31.8
02/02/99
02/02/99
CD
BFB Surrogate Recovery
%
104
104
02/02/99
02/02/99 CD
)
p-DFB Surrogate Recovery (
02/02/99
02/02/99 CD
CLB-d5 Surrogate Recovery
100
02/02/99
02/02/99 CD
J
% Solids
86.4
0.1 02/03/99
02/03/99 CD
J
r
1 SPECTRUM ANALYTICAL, INC.
Laboratory Report
Client ID: NOHO-11 Location: Atwood
Lab ID No.: AB32356 Client Job No.: J084
Matrix: Soil Preservative: Refrigeration
Collected: 01/29%99 by OTO Container: 3 Clear Glass Jars
Received on 01/29/99 by NOR Condition of Sample as Received: Satisfactory
f j QC and Data Review by Delivered by: Client
Total Hydrocarbons by GC
Modified EPA Method 8100
LLI
Parameter
Result (mg/Kg)
AML
Extracted
Analyzed
Analyst
Total Hydrocarbons (GC)
Not detected
02/02/99
02/02/99
LR
i
L
-
_
Fingerprint based quantiiicaton:
Gasoline
Not detected
40
02/02/99
02/02/99
LR
Fuel Oil #2
Not detected
40
02/02/99
02/02/99
LR
l
Fuel Oil #4
Not detected
40
02/02/99
02/02/99
LR
J
Fuel Oil #6
Not detected
80
02/02/99
02%02/99
LR
Motor Oil
Not detected
80
02/02/99
02/02/99
LR
M
Ligroin
Not detected
40
02/02/99
02/02/99
LR
Aviation Fuel
Not detected
40
.02/02/99
02/02/99
LR
~F
Other Oil
Not detected
N
d
t
d
t
80
02/02/99
02/02/99
02/02/99
02/02/99
LR
LR
Unidentified
e
ec
e
ot
~Ll % Solids ,
86.4 0.1 02/03/99 02/03/99 CD
Petroleum identification is determined by comparing the GC fingerprint obtained from the sample with a
library of GC fingerprints obtained from petroleum products. Possible match categories are as follows;
Gasoline - includes regular, unleaded, premium, etc.
Fuel Oil #2 - includes home heating oil, #2 fuel oil and diesel.
Fuel Oil #4 - Includes #4 Fuel Oil.
Fuel Oil #6 - includes #6 oil and bunker "C" oil.
Motor Oil - includes virgin and waste automobile.
Ligroin - includes mineral spirits, petroleum naphtha, vm&p naphtha.
Aviation Fuels - includes Kerosene, Jet A and JP-4.
Other Oil - includes lubricating and cutting oil and silicon oil.
n Factors such as microbial degradation, weathering and solubility generally prevent specific identification
J within a petroleum category. A finding of "unidentified" means that the sample fingerprint was characteristic of a
petroleum product, but could not be matched to a fingerprint in the library.
After fingerprint identification, the amount present in the sample is quantified using a calibration curve
prepared from a petroleum product of the same category as the identified petroleum. Unidentified petroleum
is quantified using a petroleum calibration that approximates the distribution of compounds in the sample.
A * in the results column indicates the petroleum calibration used to quantify unidentified samples.
n
!I
l _I
SPECTRUM ANALYTICAL, INC.
Laboratory Report (Subcontracted Analyses)
Client ID: N0110-11
Lab ID No: AB32356
Matrix: Soil
Collected: 01/29%99 by OTO
Received on 01/29/99 by MBR
QC and Data Review by
Location: Atwood
Client Job No: J084,
Preservative: Refrigeration
Container: 3 Clear Glass Jars
Condition of Sample as Received: Satisfactory
Delivered by: Client
~J
Parameter
Conductance
L_J
L_ J
II
LJ
J
I
j~II
Wet Chemistry Analyses .
Result 1VIDL Units
20 1.0 umhos/cm
Method
S205/E120.1
Start Date Analyst
02/01/99 PX
i
SPECTRUM ANALYTICAL, INC.
Laboratory Report
Client ID: NOHOCOMP Location: Atwood
Lab ID No: AB32390 Client Job No.: J084
J Matrix: Soil Preservative: Refrigeration
Collected: 01/29/99 b OTO Container : 2 Amber Glass Jars
Received on 01/29/99 by MBR Condition of Sample as Received: Satisfactory
n QC and Data Review by Delivered by: Client
LI
Semivolatile Organics
EPA Method 8270
Parameter for AB32390
Result (ug/Kg) MDL
Extracted Analyzed Analyst
Acenaphthene
Not detected
144.0
02/02/99
02/03/99
KS
L
Acenaphthylene
Not detected
144.0
02/02/99
02/03/99
KS
Anthracene
Not detected.
144.0
02/02/99
02/03/99
KS
Benzidine
Not detected
144.0
02/02/99
02/03/99
KS
Benzoic acid .
Not detected
720.0
02/02/99
02/03/99
KS
Benzo (a) anthracene
Not detected
144.0
02/02/99
02/03/99
KS
Benzo (b) fluoranthene
Not detected
144.0
02/02/99
02/03/99
KS
Benzo (k) fluoranthene
Not detected
144.0
02/02/99
02/03/99
KS
Benzo (g,h,i) perylene
Not detected
144.0
02/02/99
02/03/99
KS
Benzo (a) pyrene
Not detected
144.0
02/02/99
02/03/99
KS
Benzyl alcohol
Not detected
288.0
02/02/99
02/03/99
KS
Bis (2-chloroethoxy) methane
Not detected
144.0
02/02/99
02/03/99
KS
Bis (2-chloroethyl) ether
Not detected
144.0-
02/02/99
02/03/99
KS
Bis (2-chloroisopropyl) ether
Not detected
144.0
02/02/99
02/03/99
KS
Bis (2-ethylhexyl) phthalate
Not detected
144.0
02/02/99
02/03/99
KS
4-Bromophenyl phenyl ether
Not detected
144.0
02/02/99
02/03/99
KS
Butyl benzyl phthalate
Not detected
144.0
02/02/99
02/03/99
KS
4-Chloroaniline
Not detected
288.0
02/02/99
02/03/99
KS
2-Chloronaphthalene
Not detected
144.0
02/02/99
02/03/99
KS
4-Chloro-3-methylphenol
Not detected
288.0
02/02/99
02103/99
KS
2-Chlorophenol
Not detected
144.0
02/02/99
02/03/99
KS
4-Chlorophenyl phenyl ether
Not detected
144.0
02/02/99
02/03/99
KS
~J
Chrysene
Not detected
144.0
02/02/99
02/03/99
KS
Dibenz (a,h) anthracene
Not detected
144.0
02/02/99
02/03/99
KS
Dibenzofuran
Not detected
144
.0
02/02/99
02/03/99
KS
Di-n-butylphthalate
Not detected
144.0
02/02/99
02/03/99
KS
1,3-Dichlorobenzene
Not detected
144.0
02/02/99
02/03/99
KS
J
1,4-Dichlorobenzene
Not detected
144.0
02/02/99
02/03/99
KS
1,2-Dichlorobenzene
Not detected
144.0
02/02/99
02/03/99
KS
3,3'-Dichlorobenzidine
Not detected
288.0
02/02/99
02/03/99
KS
Continued next page..
Parameter for AB32390
Result (uWKg)
AML
Extracted
Analyzed
Analyst
2,4-Dichlorophenol
Not detected
144.0
02/02/99
02/03/99
KS
2,6-Dichlorophenol
Not detected
144.0
02/02/99
02/03/99
KS
Diethyl phthalate
Not detected
144.0
02/02/99
02/03/99
KS
2,4-Dimethlylphenol
Not detected
144.0
02/02/99
02/03/99
KS
4,6-Dinitro-2-methylphenol
Not detected
720.0
02/02/99
02/03/99
KS
2,4-Dinitrophenol
Not detected
720.0
02/02/99
02/03/99
KS
2,4-Dinitrotoluene
Not detected
144.0
02/02/99
02/03/99
KS
2,6-Dinitrotoluene
Not detected
144.0
02/02/99
02/03/99
KS
1,2-Diphenylhydrazine
Not detected
144.0
02/02/99
02/03/99
KS
Di-n-Propylnitrosoamine
Not detected
144.0
02/02/99
02/03/99
KS
Fluoranthene
Not detected
144.0
02/02/99
02/03/99
KS
Fluorene
Not detected
144.0
02/02/99
02/03/99
KS
Hexachlorobenzene
Not detected
144.0
02/02/99
02/03/99
KS
Hexachlorobutadiene
Not detected
144.0
02/02/99
02/03/99
KS
Hexachlorocyclopentadiene
Not detected
144.0
02/02/99
02/03/99
KS
Hexachloroethane
Not detected
144.0
02/02/99
02/03/99
KS
.Indeno (1,2,3-cd) pyrene
Not detected
144.0
02/02/99
02/03/99
KS
Isophorone
Not detected
144.0
02/02/99
02/03/99
KS
2-Methylnaphthalene
Not detected.
144.0
02/02/99
02/03/99
KS
2-Methylphenol (0-cresol)
Not detected
144.0
02/02/99
02/03/99
KS
4-Methylphenol (p-cresol)
Not detected
144.0
02/02/99
02/03/99
KS
Naphthalene
Not detected.
144.0
02/02/99
02/03/99
KS
2-Nitroaniline
Not detected
720.0
02/02/99
02/03/99
KS
3-Nitroaniline
Not detected
720.0
02/02/99
02/03/99
KS
4-Nitroaniline
Not detected
720.0
02/02/99
02/03/99
KS
Nitrobenzene
Not detected
144.0
02/02/99
02/03/99
KS
2-Nitrophenol
Not detected
144.0
02/02/99
02/03/99
KS
.4-Nitrophenol
Not detected
720.0
02/02/99
02/03/99
KS
N-Nitrosodimethylamine
Not detected.
144.0
02/02/99
02/03/99
KS
N-Nitrosodiphenylamine
Not detected
144.0
02/02/99
02/03/99
KS
Pentachlorophenol
Not detected
720.0
02/02/99
02/03/99
KS
Phenanthrene
Not detected
144.0
02/02/99
02/03/99
KS
Phenol
Not detected
144.0
02/02/99
02/03/99
KS
Pyrene
Not detected
288.0
02/02/99
02/03/99
KS
1,2,4-Trichlorobenzene
Not detected
144.0
02/02/99
02/03/99,
KS
2,4,5-Trichlorophenol
Not detected
144.0
02/02/99
02/03/99
KS
2,4,6-Trichlorophenol
Not detected
144.0
02/02/99
02/03/99
KS
Pyridine
Not detected
144.0
02/02/99
02/03/99
KS
Dimethyl phthalate
Not detected
144.0
02/02/99
02/03/99
KS
Di-n-octyl phthalate
Not detected
144.0
02/02/99
02/03/99
KS
SPECTRUM ANALYTICAL, INC.
Laboratory Report
Client ID: NOHOCOMP Location: Atwood
Lab ID No.: AB32390 Client Job No.: J084
Matrix: Soil Preservative:
Collected: 01/29/99 by OTO Container:
Received on 01/29/99 by MBR Condition of Sample as Received: Satisfactory
n QC and Data Review by Delivered by: Client
Volatile Organics
EPA Method 8260
Parameter for AB32390
Result (ug/Kg)
AML
Extracted
Analyzed
Analyst
Benzene
Not detected
6.1
02/02/99
02/02/99
CD
Bromobenzene
Not detected
6.1
02/02/99
02/02/99
CD
Bromochloromethane
Not detected
6.1
02/02/99
02/02/99
CD
Bromodichloromethane
Not detected
6.1
02/02/99
02/02/99
CD
Bromoform
Not detected
6.1
02/02/99
02/02/99
CD
n-Butylbenzene
Not detected
6.1
02/02/99
02/02/99
CD
sec-Butylbenzene
Not detected
6.1
02/02/99
02/02/99
CD
tert-Butylbenzene
Not detected
6.1
02/02/99
02/02/99
CD
Carbon tetrachloride
Not detected
6.1
02/02/99
02/02/99
CD
Chlorobenzene
Not detected
. 6.1
02/02/99
02/02/99
CD
Chloroform
Not detected
6.1
02/02/99
02/02/99
CD
2-Chlorotoluene
Not detected
6.1
02/02/99
02/02/99
CD
4-Chlorotoluene
Not detected
6.1
02/02/99
02/02/99
CD
1,2-Dibromo-3-chloropropane
Not detected
6.1
02/02/99
02/02/99
CD
Dibromochloromethane
Not detected
6.1
02/02/99
02/02/99
CD
1,2-Dibromoethane (EDB)
Not detected
6.1
02/02/99
.02/02/99
CD
Dibromomethane
Not detected
6.1
02/02/99
02/02/99
CD
1,2-Dichlorobenzene
Not detected
6.1
02/02/99
02/02/99
CD
1,3-Dichlorobenzene
Not detected
6.1
02/02/99
02/02/99
CD
1,4-Dichlorobenzene
Not detected
6.1
02/02/99
02/02/99
CD
1,1-Dichloroethane
Not detected
6.1
02/02/99
02/02/99
CD
1,2-Dichloroethane
Not detected
6.1
02/02/99
02/02/99
CD
1,1-Dichloroethene
Not detected
6.1
02/02/99
02/02/99
CD
cis-1,2-Dichloroethene
Not detected
6.1
02/02/99
02/02/99
i
CD
trans-l,2-Dichloroethene
Not detected
6.1
02/02/99
02/02/99
CD
1,2-Dichloropropane
Not detected
6.1
02/02/99
02/02/99
CD j
1,3-Dichloropropane
Not detected
6.1
02/02/99
02/02/99
CD
2,2-Dichloropropane
Not detected
6.1
02/02/99
02/02/99
CD 4
Continued next page..
Parameter for AB32390
Result (ug/Kg)
MDL
Extracted
Analyzed
Analyst
1,1-Dichloropropene
Not detected
6.1
02/02/99
02/02/99
CD
cis-1,3-Dichloropropene
Not detected
6.1
02/02/99
02/02/99
CD
trans-1,3-Dichloropropene
Not detected
6.1
02/02/99
02/02/99
CD
Ethylbenzene
Not detected
6.1
02/02/99
02/02/99
CD
Hexachlorobutadiene
Not detected
6.1
02/02/99
02/02/99
CD
Isopropylbenzene
Not detected
6.1
02/02/99
02/02/99
CD
4-Isopropyltoluene
Not detected
6.1
02/02/99
02/02/99
CD
Methylene chloride
Not detected
6.1
02/02/99
02/02/99
CD
Naphthalene
Not detected
6.1
02/02/99
02/02/99
CD
n-Propylbenzene
Not detected
6.1
02/02/99
02/02/99
CD
Styrene
Not detected
6.1
02/02/99
02/02/99
CD
1,1,1,2-Tetrachloroethane
Not detected
6.1
02/02/99
02/02/99
CD
1,1,2,2-Tetrachloroethane
Not detected
6.1
02/02/99
02/02/99
CD
Tetrachloroethene
Not detected
6.1
02/02/99
02/02/99
CD
Toluene
Not detected
6.1
02/02/99
02/02/99
CD
1,2,3-Trichlorobenzene
Not detected
6.1
02/02/99
02/02/99
CD
1,2,4-Trichlorobenzene '
Not detected
6.1
02/02/99
02/02/99
CD
1,1,1-Trichloroethane
Not detected
6.1
02/02/99
02/02/99
CD
1,1,2-Trichloroethane
Not detected_
6.1
02/02/99- -
- 02/02/99
CD
Trichloroethene
Not detected
6.1
02/02/99
02/02/99
CD
Trichlorofluoromethane
Not detected
6.1
02/02/99
.02/02/99
CD
1,2,3-Trichloropropane
Not detected
. 6.1
02/02/99
02/02/99
CD
1,2,4-Trimethylbenzene.
Not detected
6.1
02/02/99
02/02/99
CD
1,3,5-Trimethylbenzene
Not detected
6.1
02/02/99
02/02/99
CD
m,p-Xylenes
Not detected
12.2
02/02/99
02/02/99
CD
o-Xylene
Not detected
6.1
02/02/99
02/02/99
CD
Methyl-t-butyl ether
Not detected
6.1
02/02/99
02/02/99
CD
BFB Surrogate Recovery
%
101
105
02/02/99
02/02/99
CD
)
p-DFB Surrogate Recovery (
02/02/99
02/02/99
CD
CLB-d5 Surrogate Recovery
98
02/02/99
02/02/99
CD
% Solids
89.7
01 02/03/99
02/03/99
GMM
U
n
J
-
- - -
SPECTRUM ANALYTICAL, INC.
Laboratory Report
Client ID: NOHOCOMP Location: Atwood
Lab ID No.: AB32390 Client Job No.: J084
Matrix: Soil Preservative: Refrigeration
Collected: 01/29%99 by OTO Container: 2 Amber Glass Jars
Received on 01/29/99 by MBR Condition of Sample as Received: Satisfactory
QC and Data Review by Delivered by: Client
Total Hydrocarbons by GC
L-A Modified EPA Method 8100
Parameter Result (mg/Kg) MDL
Extracted Analyzed Analyst
Total Hydrocarbons (GC) Not detected 02/02/99 02/02/99 LR
Fingerprint based quantificaton:
a
Gasoline
Not detected
40
02/02/99
02/02/99
LR
Fuel Oil #2
Not detected
40
02/02/99
02/02/99
LR
I~1
Fuel Oil #4
Not detected
40
02/02/99
02/02/99
LR
I~
Fuel Oil #6
Not detected
80
02/02/99
02/02/99
LR
Motor Oil
Not detected
80
02/02/99
02/02/99
LR
Ligroin
Not detected
40
02/02/99
02/02/99
LR
~J .
Aviation Fuel
Not detected
40
02/02/99
02/02/99
LR
Other Oil
Not detected
80
02/02/99
02/02/99
LR
Unidentified
Not detected
02/02/99
02/02/99
LR
1
% Solids
89.7
0.1
02/03/99
02/03/99
GMM
Petroleum identification is determined by comparing the GC fingerprint obtained from the sample with a
library of GC fingerprints obtained from petroleum products. Possible match categories are as follows;
11 Gasoline - includes regular, unleaded, premium, etc.
L Fuel Oil #2 - includes home heating oil, #2 fuel oil and diesel.
Fuel Oil #4 - Includes #4 Fuel Oil.
Fuel Oil #6 - includes #6 oil and bunker "C" oil.
u Motor Oil - includes virgin and waste automobile.
Ligroin - includes mineral spirits, petroleum naphtha, vm&p naphtha.
Aviation Fuels - includes Kerosene, Jet A and JP-4.
Other Oil - includes lubricating and cutting oil and silicon oil.
Factors such as microbial degradation, weathering and solubility generally prevent specific identification
within a petroleum category. A finding of "unidentified" means that the sample fingerprint was characteristic of a
petroleum product, but could not be matched to a fingerprint in the library.
After fingerprint identification, the amount present in the sample is quantified using a calibration curve
prepared from a petroleum product of the same category as the identified petroleum. Unidentified petroleum
is quantified using a petroleum calibration that approximates the distribution of compounds in the sample.
A * in the results column indicates the petroleum calibration used to quantify unidentified samples.
SPECTRUM ANALYTICAL, INC.
l Laboratory Report (Subcontracted Analyses)
Client ID: NOHOCOMP Location: Atwood
Lab ID No: AB32390 Client Job No: J084
Matrix: Soil Preservative: Refrigeration
Collected: 01/29%99 by OTO Container: 2 Amber Glass Jars
Received on 01/29/99 by MBR Condition of Sample as Received: Satisfactory
r~ QC and Data Review by Delivered by: Client
Wet Chemistry Analyses
Parameter Result MDL Units Method Start Date Analyst
n Conductance 56 1.0 umhos/cm S205/E120.1 02/01/99 PX
LJ
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Spectrum Analytical, Inc.
Laboratory Report Supplement
- References
Methods for the Determination of Organic Compounds in Drinking Water. EPA-600/4-88/039. EMSL 1988.
Methods for Chemical "Analysis of Water arid Wastes. EPA 600/4-79-020. EMSL 1983.
i Methods for Organic Chemical Analysis of Municipal and Industrial Wastewater. EPA 600/4-82-057. EMSL 1982.
Test Methods for Evaluating Solid Waste. Physical/Chemical Methods. EPA SW-846. 1986.
Standard Methods for the Examinatinon of Water and Wastes. APHA-AWWA-WPCF. 16fh-Edition. 1985.
Standard Methods for Comparison of Waterborne Petroleum Oils by Gas Chromatography. ASTM D 3328. 1982.
u
Oil Spill Identification System. U.S. Coast Guard CG-D-52-77. 1977.
_J Handbook for Analytical Quality Control in Water and Wastewater Laboratories. EPA 600/4-79-019. EMSL 1979.
Choosing Cost-Effective QA/QC (Quality Assurance/Quality Control) Programs for Chemical Anslyses. EPA 600/4-85/056.
a EMSL 1985.
Report Notations
D Not Detected, = The compound was not detected at a concentration equal to or above
Not Det, ND or nd the established method detection limit.
NC = Not Calculated
MCL EPA Maximum Contamination Level
VOA Volatile Organic Analysis
BFB 4-Bromofluorobenzene : (An EPA 624 Surrogate)
p-DFB _ 1,4-Diuorobenzene (An EPA 624 Surrogate)
CLB-d5 Chlorobenzene-di (An EPA 624 Surrogate)
BCP = 2-Bromo-l-chloropropane (An EPA 601 Surrogate)
TFT = a,a,a-Triuorotoluene (An EPA 602 Surrogate)
Decachlorobiphenyl (an EPA 60818080 Surrogate)
Definitions
U Surrogate Recovery = The recovery (expressed as a percent) of a non-method analyte (see surrogates listed
above) added to the sample for the purpose of monitoring system performance.
Matrix Spike Recovery = The recovery (expressed as a percent) of method analytes added to the sample for the
I~ purpose of determining any effect of sample composition on analyte recovery.
Laboratory Replicate = Two sample aliquots taken in the analytical laboratory and analyzed separately with
identical procedures. Analyses of laboratory duplicates give a measure of the preceision associated with
laboratory procedures, but not with sample collection, preservation, or storage procedures.
Field Duplicate = Two separate samples collected at the same time and place under identifical circumstances and
treated exactly the same throughout field and laboratory procedures. Analysis of Field duplicates give a measure
of the precision associated with sample collection, preservaton and storage, as well as with laboratory procedures.
r-1
Relative Percent Difference RPD) = The precision measurement obtained on duplicate/replicate analyses.
%RPD is calculated as:
.%RPD (valuel - value2) * 100° o
aver value_
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SPECTRUM ANALYTICAL, INC.
Massachusetts Certification M-MA 138
Connecticut Approval # PH 0777
Rhode Island # 98 & Maine n/a
New Hampshire ID # 2538
New York ID #11393
Florida HRS87448
O'Reilly, Talbot & Okun
293 Bridge Street, Suite 500
Springfield, MA 01103
June 2, 1999
Client Project No.: 84-05-17 Location: Atwood Drive - Northampton, MA
Lab ID No. Client ID
AB44666 STOCK-1
J
Analysis Requested
TCLP Lead
ENVIRONMENTAL ANALYSES
Almgren Drive Agawam; Massachusetts 01001-c,-413--789-9018----FA-X-413-789-4076-
- - - - - -
SPECTRUM ANALYTICAL, INC.
Laboratory Report (Subcontracted Analysis)
Location: Atwood Drive - Northampton, MA
Client Job No: 84-05-17
L_ Client-ID: STOCK-1
n Lab ID No: AP44666
J Matrix: Soil
Collected: 05/27/99 by OTO
Received on 05/27/99 by KC
j QC and Data Review by MD
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Parameter
1
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Container: 1 Amber Glass
Condition of Sample as Received: Satisfactory
Delivered by: Client
TCLP Lead
EPA Method 1311/SW846 6010
Result (mg/L)
3.23
MDL
Extracted Analyzed
0.010 06/01/99 06/02/99
Analyst
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Massachusetts Department of Environmental Pratectlon
Bureau of Waste Site Cleanup
SILL OF LADING (Pursuant to ago cMR ao.aoao) >JRA
A. LOCATION OF SITE OR DISPOSAL SITE WHERE. REMEDIATION WASTE WAS GENERATED:
Release Name (optional):
Street: Atwood Driye ...Location Aid: End of Cul-de-sac
City/Town: Northampton Zip Coder ' 01060
rl -
Date/Period-of Generation:. 5 / 2 7 / 9 9 to _
Additional Release Tracking Numbers Associated with this Bill of Lading:
Note: if this Bill of Lading Is the result of a Limited RemovafAction (LRA) taken prior to-Madflcation, a Release Tracking
. Number is not needed .
I B. PERSON CONDUCTING RESPONSE ACTION ASSOCIATED WITH BILL OF LADING:
Name of Organization: City of Northcim:oton
J Name of Contact: Via= n e F P i ci r--n Title:
I Street. r-i i-~ Ha 11 , 21 n' Ma inStreet
_
1 City/Town: Northampton State: MA 'Zip Code: 01060
l Telephone: 413 -5 8 7 - 1 2 6 5 Ext.
C. RELATIONSHIP TO RELEASE OR THREAT OF RELEASE OF PERSON CONDUCTING RESPONSE ACTION
ASSOCIATED WITH BILL OF,LADING:.
(check one/specify)
I ❑ RP ,Specify (circle one): Owner Operator ...Generator. ..Transporter Other. RP:.
1 ® PRP Specify (circle one): Owner Operator, • Generator Transporter. Other PRP:
J Fiduciary/Secured Lender
❑ Agency/Public Utility on a Right of Way
J ❑ Other Person: ;
fJ If an owner and/or operator is not conducting the response action associated with the Bill of Lading, provide on an attachment the name, contact
person. address and telephone number, including any area-code and extension, for each,"If known. '
D-TRANSPORTER/COMMON CARRIER INFORMATION: .
1 rs~, C .
J Transporter/Common Carrier Name: J. ~ ~ te;`5 S A
Contact Person: ~~~t i~ J s of ~`_c'
Title:
Street
City/Town: 1--. i~ State: Zap Code: 0 ,,tiJ Z 0 _
Telephone: Ext.
E. RECEIVING FACILITYITEMPORARY STORAGE LOCATION:
I
. Operator/FacilttyName: City :of Northampton Landfill
:
Contact Person: Peter McErlail
Titie Health Aaent
- street: Board of Health ; 210 MIN-.Street.
"
I City/Town' Northamptoft' MA °
State:
01060
Zip Code: _
Telephone:`/; _545' - % lye .ExL
Type of Facifty'. ❑ Asphalt Batoh/Cold Mix. ❑ Landfill/Disposal
❑ incinerator .
(check one) ❑ Asphalt Batah/Hot Mix ® Landfill/Daily Cover
❑ Temporary
❑ Thermal Processing ❑ Landfill/Structural Fill
❑ Storage
_
Other:
Division of Hazardous ' Division of Solid Waste.
Waste/Class A Permit Management Permit 96-214-002 EPA Identification
Actual/Anticipated Period of Temporary Storage (specify dates if applicable): NA
to
NA
Reason for Temporary Storage (if applicable):
Massachusetts Department of.iEnvironrnenta9 Protection BWSC-012A
Bureau of Waste Site Cleanup Reim.
rl
~ i _ LRA
l , 9 BILL OF LADING'(pursuant to 310 CZAR 40.0030)
H. CERTIFICATION OF PERSON CONDUCTING RESPONSE ACTION ASSOCIATED WITH THIS BILL OF LADING:
I certify under penalties of law that I have personally examined and am familiar with the information contained in this submittal, Including-any and
I all documents accompanying this certification, and that, based on my inquiry of those Individuals immediately responsible -for obtaining the
information, the material information dontained herein is, to the best of my knowledge and belief, true, accurate and-complete. I am aware that
there are significant penalties, Including, but not limited. to, possible. fines. arid. imprisonment, for wilfully submitting false, inaccurate, or
incomplete information.
r
F Signature: ?r'~ y'r~'A.-~* Gate: ~ I l
I Name of Person (print):~~`iG
* As Agent for the City of Northampton
evts
Tins form is printed on racy-cled paper. 1-age ;s or
i
Massachusetts Department of Environm
M
ental Protection BWSC-012B
Bureau of Waste Site Cleanup . .
Rele"e Tr=Wnq Nunjbw
H
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DILL OF LADING (pursuant to 310 CMR 40.0030)
LRA
LOG SHEET OF
1. LOAD INFORMATION:
LOAD 1: Signature of Transporter Representative:
Receivin
Facillty/Temporary Storage Representative:
g
Date of Shipment: Time of'Shipment:
Date of Receipt:. Time of Receipt:
(circle one) am/pm
: s .
i /4-
Truckfrractor Registration: Trailer Registration (if any):
.
"
(circle one) am/pm
.i_
i
-
; Load Size (cu. yds./tons):
LOAD 2: Signature of Transporter Representative:
Receiving Facility/Temporary Storage Representative:
Date of Shipment: Time of Shipment:
t
i Date of Receipt: Time of Receipt:
(circle one) am/pm
Truck/Tractor Registration : Trailer Registration Cif any):
i (circle one) am/pm
Load Size (cu. ydsJtons):
LOAD 3: Signature of Transporter Representative:
Receiving Facility/Temporary Storage Representative:
i
Date of Shipment: Time of Shipment:
i
Date of Receipt: Time of Receipt:
(circle one) am/pm
It
Truck/Tractor Registration: Trailer Registration (if any):
(circle one) am/pm
Load Size (cu. ydsJtons):
LOAD 4: Signature of Transporter Representative:
i Receiving Facility/Temporary Storage Representative:
Date of Shipment: Time of Shipment: • `
i
i Date of Receipt: Time of Receipt:
(circle one) am/pm
Truck/Tractor Registration: Trailer Registration (if any):
(circle one) am/pm
t Load Size (cu. ydsJtons):
LOAD 5: Signature of Transporter Representative:,
i Receiving Facifity/Temporary Storage Representative:
Date of Shipment: Time.of Shipment:
i Date of Receipt: Time of Receipt: .
(circle one) am/pm
1
i
Truck/Tractor Registration:.- Trailer Registration (if.any):
I . (circle one) am/pm
'Load Size (cu. ydsJfons-j:
LOAD 6: Signature of Transporter Representative:
Receiving Facllity/Temporary Storage Representative:
Date of Shipment: Time of Shipment
i
i Date of Receipt: Mme of Receipt:
_ (circle one) am/pm:'
TruckR ractor Registration: Trailer Registration, (if any):.
(circle one) am/pm
Load Size (cu. ydsJtons):
LOAD 7: Signature of Transporter Representative:
Receiving Facility/Temporary Storage Representative:
Date of Shipment: Time of Shipment -
i Date of Receipt: Time of Receipt:
(circle one) aMpm`
1
_ /
-T-ruck/Tractor Registration: Trailer Registration (f any):
(circle one) am/pm
r
j Load Size (cu. ydsJtons):
J J. LOG SHEET VOLUME INFORMATION:
Total Volume This Page (cu.ydsAons):
l Y
Total Carried Forward (cu.ydsAons):
Total Carried Forward and This Page(cu.yds.ttons):
lrS
evise 10/1/94 1 tits r is nn paper. Page 1 of 1
Massachusetts Department of Environmental Protection BWSC-012C
Bureau of Waste Site Cleanup
BILL OF LADING (pursuant 10 310 CMR 40.0030) a TiadHnp tdumber
SUMMARY SHEET OF -LRA.
K -''SUMMARY'OF SH
IPMENTS:.
DATE OF SHIPMENT:
DATE OF RECEIPT:
NUMBER OF LOADS SHIPPED:
DAILY VOLUME SHIPPED (CU, YDS,/TONS):
- - - - - - - - - - - - - - - -
- - - - - - - - - - - - - - - -
- - - - - - - - - - - - - - - -
- -
- - - - - - - - - -
- - - - - - - - -
- - - - - - - - - - - - - - - - -
- - - - - - - - - - - -
- - - - - - - - - -
-
-
- - - -
- - - - - - - - - - - - - - - - - - - - - - - - - - -
- - - - - - - - - - - - - - - - - - - - - - - - - - -
- - - - - - - - - - - - - - - - - - - - - - - - - - - - -
- - - - - - - - - - - - - - - - - - - - - - - - - - - -
- -
- - - - - - - - - - - - - - - - - - - - - - - - - - - - -
-
- - - - - - - - - - - - - - - - - - - - - - - - - - - - -
- - - - - - - - - - - - - - - - - - - - - - - - - - - - -
- - - - - - - - - - - - - - - - - - - - - - - - -
- - - - - - - - - - - - - - - - - - - - - - - - - - -
- - - - - - - - - - - - - - - - - - - - - - - - - - - -
-
- - - - - - - - - - - - - - - - - - - - - - - -
SUMMARY SHEET TOTAL SHIPPED:
BILL OF LADING TOTALSHIPPED (only if different):
R ' ed° 10/1194
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WASTE MANAGEMENT [ `310N
MICHIGAN DEPARTMEN-f OF
ENVIRONMENTAL QUALITY
F1
Please print or type.
_ cyuucu uuue, euuwrny u1 tart i anu
art 121 of Act 451, 1994, as amended.
Failure to file may subject you to
DO NO-OWRITE IN THIS t.OE criminal and/or civil penalties under
'ATT. ❑ DIS. El REJ. El PR. El Sections 324.11151 or 324.12116 MCL.
Form Approved.- OMB No. 2050-0039
UNIFORM HAZARDOUS
1 G n~e atrgr's U EXA ID No. Manifest
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Information in the shaded areas
WASTE MANIFEST
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of
isawnot. required by Federal
3. Generator's Name and Mailing Addr ss -
CITY OF NORTRAHPi N ~„~~y
A .State ManlfestDocur
'hent Number
. NORT'HAXPTOB
210 MAIN ST
MA 01060
~
'
,
:,B'.1 State Generator's ID'-.- .ATWOO?2 DR~
4. Generator's Phone ( 413 1 587--1265
INORTHA 'SON hA
5. Transporter 1 Company Name 6. US EPA ID Number
1 AD 985 294 693
OIL RECOVERY CORP
E.; State ,Transporter s !D . ,
.
D.;Transporters Flione4i3 737-2949
7. Transporter 2 Company Name 8. US EPA ID Number
'E_State Transporters ID
F. Jrarisporter!s' Phone
9. Designated Facility Name and Site Address 10. US EPA ID Number
G. State Facility's ID
CHFA-MT SERVICES INC.
18550 ALLEN
B
RO
_ . ~ .
HC I aclli 's Phone""
SRGvt STC , 48192 KID 096 563 194
' 734-2~2-925 3
11. US DOT Description (including Proper Shipping Name, Hazard Class, and
12. Containers
13.
Total
14.
Unit
i. Waste
No
J
ID NUMBER).
HM
No. T e
Quanti
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R.Q,RAZA OUS WASTE SOLID, N.,O. S. s (I)€ 0,5 ,LEAD) s 9 s
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fL Handling Codes
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15. Special Handling Instructions and Additional Information
t ERG #171 24 HR. FEO11E:517--523--7740 SEND COPY OF qIF. WWI V'
16. GENERATOR'S CERTIFICATION: Thereby declare that the contents of this consignment are fully and accurately described above by propel'shipping name and are classified,
packed, marked, and labeled, and are in all respects in proper condition for transport by, Ighway according to applicable international and national government regulations.
If I am a large quantity generator, I certify that I have a program in place to reduce the volume and toxicity of waste generated to the degree l .have determined
to be economically practicable and that I have selected the practicable method of treatment,' storage, or disposal currently available to me which minimizes the
present and'future threat to humah health and the environment;, OR; if I am a small-quantity generator, I have made a good faith effort to minimize my waste
generation and select the best waste management method that is available to me and that I .can afford.
F Date
Printed/Typed Name
Signature Month Day Year
/
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17. Transporter 1 Acknbwle
ement of Receipt of Mat ' Is v
r.
Date
q'
Prihted/Typ ! , f r'1 V !J
Signa "tiT°%/ 1
IN
>
S
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18. Transporter 2 Acknowledgement of Receipt of Materials - Date
T
Printed/Typed Name
Signature
Month Day Year
E
R
19. Discrepancy Indication Space
F
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20. Facility Owner or Operator: Certification of receipt of hazardous materials covered by this manifest except as noted in
I
Item 19. Date'
y
Pripted(ryped Name i Signature Month Day Year
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CHEM-MET SEkVICES 046142
ME= 18550 ALLEN ROAD Phone -925
.734-282 0
BROWNSTOWN, M1 48192
EPA # MID096963194
CERTIFICATE OF DISPOSAL
This certifies that the waste(s) specified on MANIFEST NUMBER : M17404681
FOR GENERATOR: MA RC10001051 c AND TRANSPORTER: MAD985294693
NORTHHAMPTION, CITY OF OIL RECOVERY CORPORATION
201 MAIN ST.
ATWOOD DR.
NORTHHAMPTON, MA 010FIO
has been properly disposed of under the authority of all required and applicable permits and licenses,
to my best knowledge and belief based on my inquiry of individuals immediately responsible for the
waste disposal.
The waste identified above has been handled -in compliance with one or more of the
applicable performance standards specified in 40 CFR, part 268, subpart D and all applicable
prohibitions set forth in 40 CFR 268.32 or RCRA section 3004 (d).