HomeMy WebLinkAboutAGM:Glass Sand, Waste Mgmt Testing, Approvals Contract New York 'State Department of Environmental Conservation
Division of Solid & Hazardous Materials, Region One
Building 40 - SUNY, Stony Brook, New York 11790-2356 _
Phone: (516) 444-0375 FAX: (516) 444-0231
John P. Cahill
Commissioner
August 10, 1999
The Honorable Jean W. Cochran
Supervisor Town of Southold
Town Hall
.59095 Main Road -
Southold,New York 11971
Dear Supervisor Cochran:
The New York State Department of Environmental Conservation("Department")recently had an
opportunity to visit the Waste Management facilities in Brooklyn NY which manufacture the glass sand
being used in the Southold Landfill as grading material beneath the liner. What came to light during this
inspection was that Waste Management does not have sufficient space at that facility to stockpile glass sand
prior to shipping the material to Southold.
Because the landfill is closed and no longer can accept material for disposal,it is necessary that the
Department approve all materials being brought into the landfill for grading if they are not clean soils and
sands. To help minimize the costs, the Department agrees to allow Waste Management to stockpile glass
sand on the Southold landfill grounds prior to its sampling and being used for grading. The stockpiles must
be staged within the footprint of the landfill.
Glass sand will be stockpiled to approximately 5000 cubic yards at which time a representative
sample will be collected and analyzed. A sampling plan will be generated by Town consulting engineers
Dvirka and Bartilucci,agreed to by Waste Management and approved by the Department prior to any glass
sand shipment. In the event that the material is not suitable for use as grading material at Southold landfill,
Waste Management will remove and properly dispose of it at their own expense in a timely fashion. Once
a pile is sampled, no new material shall be added to it. Any new glass sand brought to Southold will be
placed into another or second pile to begin accumulation. Once approval is given by the Department,that
pile may be used for grading.
If there are questions,please contact the undersigned at 516-444-0388.
Sincerely,
�Pmest Lampro J�
Environmental Engineer I
cc: Alice Hussie,Town of Southold
Gregory Yakaboski,Town of Southold
James Bunchuck,Town of Southold
Tara Hemmer,Waste Management of New York
Melissa Treers,NYSDEC,Albany
David Glass,D&B
file: 52S17
:.9
0 •
New York State Department of Environmental Conservation AM
Division of Solid & Hazardous Materials, Region One aftlow
Building 40 - SUNY, Stony Brook, New York 11790-2356 _
Phone: (516) 444-0375 FAX: (516) 444-0231
John P. Cahill
Commissioner
June 16, 1999
The Honorable Jean W. Cochran
Supervisor Town of Southold
Town Hall
59095 Main Road
Southold,New York 11971
Dear Supervisor Cochran:
The New York State Department of Environmental Conservation (Department) is in receipt of a
June 9, 1999 fax of a chain of custody and the analytic data from a sample of crushed glass sand from Mr.
James Bunchuck. This glass sand sample was reported to have been collected on May 11, 1999 from glass
sand material at the Waste Management Brooklyn facility on Thomas Street. It is intended to use this
material in the Southold Landfill as grading material.
The Department has no objection to the use of this material at the Southold Landfill for grading
purposes beneath the liner.
If there are any questions please contact me at 516-444-0388.
Sincerely,,
4e�41 ,,
'.e
4, ,�W/rl;p- 't)
Ernest Lampro Jr.
Environmental Engineer I
cc: Alice Hussie,Town of Southold
Gregory Yakaboski,Town of Southold
James Bunchuck,Town of Southold
Melissa Treers,NYSDEC,Albany
Tom Maher,D&B
David Glass,D&B
file: 52S17
New York State Department of Environmental Conservation
Division of Solid & Hazardous Materials, Region One
Building 40 - SUNY, Stony Brook, New York 11790-2356 _
Phone: (516) 444-0375 FAX: (516) 444-0231
John P. Cahill
Commissioner
June 4, 1999
The Honorable Jean W. Cochran
Supervisor Town of Southold
Town Hall
59095 Main Road
Southold,New York 11971
Dear Supervisor Cochran:
The New York State Department of Environmental Conservation (Department) has received and
reviewed the analytical results from the May 14, 1999 sampling of the glass sand material currently on the
Southold landfill. Both the`old pile"and the"new pile"are acceptable for use as grading material beneath
the liner of the landfill.
The Department has approved in an August 12, 1998 letter,the use of Waste Management generated
glass sand beneath the liner for grading of the Southold Landfill. At that time certain restrictions were placed
on the acceptance and use of the material. However, the Department,at that time,did not require periodic
analysis of the material. To correct this and prevent any future occurrence of the events which led to the
need to perform the May 14 sampling,the Department will require a full analysis of the glass sand material
for every 10,000 - 12,000 cubic yards brought to the Southold landfill. The analytical results should be
reviewed by the Town of Southold and the Department prior to any of the material being brought to the
landfill.
If there are any questions please contact me at 516-444-0388.
Sincerely,
Ixnd�2 �
Ernest Lampro Jr.
Environmental Engineer I
cc: Alice Hussie,Town of Southold
Gregory Yakaboski,Town of Southold
James Bunchuck,Town of Southold
Melissa Treers,NYSDEC,Albany
Tom Maher,D&B
David Glass,D&B
file: 52S17
Dvirka
and
0 Bartilucci
CONSULTING ENGINEERS
330 Crossways Park Drive,Woodbury, New York, 11797-2015
516-364-9890 ■ 718-460-3634 ■ Fax:516-364-9045
e-mail: db-eng@woridnet.att.net
May 26, 1999
Ernest Lampro, Jr.
New York State Department of Environmental Conservation
Division of Solid&Hazardous Materials, Region One
Building 40—SUNY
Stony Brook, New York 11971
Re: Southold Landfill
Glass Sand Sampling
D&B No. 1314-F1
Dear Mr. Lampro:
Enclosed please find the results of the analytical testing which you requested for the glass sand at
the Southold Landfill. As you know two piles were sampled on May 14, 1999.
Four grab samples, one from each side, were collected from the pile near the former lagoon (the
"New Pile"). The grab samples were collected at a depth of approximately 3 feet from the
surface of the pile. Since staining and odors were observed, as directed, a portion of one of the
four grab samples was tested for volatile organic compounds (VOCs). In addition, the remainder
of the grab sample tested for VOCs and the other three grab samples were composited by the
laboratory and tested for metals, cyanide, semivolatile organic compounds, PCBs, pesticides and
herbicides.
Two grab samples were collected from the pile near the high voltage electric line tower(the"Old
Pile"). The grab samples were collected at a depth of approximately 3 feet from the surface of
the pile and composited by the laboratory. The composite sample was tested for metals.
On the enclosed tables the results are compared to the recommended soil cleanup objectives in
TAGM 4046 (Determination of Soil Cleanup Objectives and Cleanup Levels). The
concentrations of zinc detected in both samples (i.e., 87 mg/kg and 61 mg/kg) slightly exceed the
TAGM value of 20 mg/kg; however, this is an extremely conservative cleanup level. The
semivolatile organic compound phenol was reported at a concentration of 1,500 ug/kg in the
composite sample collected from the New Pile. This exceeds the cleanup level for phenol of 30
ug/kg; however, the result was qualified by the laboratory as an estimated value since it was
detected below the contract required detection limit. In addition, the total concentration of
semivolatile organic compounds detected in the composite sample from the New Pile is 19,870
ug/kg, which is well below the TAGM criteria of 500,000 ug/kg.
A DIVISION OF WILLIAM F.COSULICH ASSOCIATES,P.C.
OVIRKA AND BAATILUCCI
Ernest Lampro,Jr. Page Two
New York State Department of Environmental Conservation
Division of Solid&Hazardous Materials, Region One
May 26, 1999
Based on our review of these results, the material is acceptable for the intended use as general
fill/contour grading material to be placed below the gas venting layer and HDPE geomembrane
of the landfill cap. Please contact me at your earliest convenience with your determination so
that the Town can start accepting the glass sand again and complete the effort of filling in the
former lagoon.
If you have any questions regarding this matter or require additional information, please do not
hesitate to contact me.
Very truly yours,
Thomas F. Maher,PE
Vice President
TFM/DSGt/kd
cc: Jean Cochran, Supervisor,Town of Southold
James Bunchuck, Town of Southold
David Glass,Dvirka and Bartilucci
♦1314/tfm99-16.1tr.(R0l)
TABLE 1
SOUTHOLD LANDFILL
GLASS SAND SAMPLING RESULTS
METALS AND CYANIDE
SAMPLE InFINITIFICATION NP-COMP QP-CQMP RECOMMENDED EASTERN
DATF OF C-01 I Fr-TIQN 0511419R. 05/14/99 SOIL USA
CLEANUP BACKGROUND
PFRCFNT Sol IDS 0 0
Aluminum 580 370 SB 33000
Antimony U U SB —
Arsenic U U 7.5 or SB 3- 12*
Barium 82 26 300 or SB 15-600
Beryllium U U 0.16 or SB 0-1.75
Cadmium 0.6 U 10 or SB 0.1 -1,(10'**)
Calcium 1400 1600 SB 130-35000
Chromium 3 3 50 or SB 1.5-40-,(50***)
Cobalt U U 30 or SB 2.5-60
Copper 12 8 25 or SB 1 -50
Iron 750 400 2000 or SB 2000-550000
Lead 35 44 SB 200-500**
Magnesium 220 400 SB 100-5000
Manganese 58 26 SB 50-5000
Mercury U U 0.1 0.001 -0.2
Nickel 6 U 13 or SB 0.5-25
Potassium U U SB 8500-43000
Selenium U U 2 or SB 0.1 -3.9
Silver U U SB —
Sodium 600 310 SB 6000-8000
Thallium U U SB —
Vanadium I I 1 11 150 or SB 1 -300
Zinc R7 A 1 20 or SB 9-550 •
Qualifiers: Notes:
U:Compound analyzed for but not detected. — : Not established.
NT: Not tested for. : New York State Background.
SB:Site Background. ** : Background for metropolitan or suburban areas.
*** : Proposed revised criteria for cadmium and
chromium in TAGM 4046 Appendix A.
M: Exceeds Recommended Soil Cleanup Objective.
SOUTHMETAM/mr 05126/99
TABLE 2
SOUTHOLD LANDFILL
GLASS SAND SAMPLING RESULTS
VOLATILE ORGANIC COMPOUNDS
SAMPLE IDENTIFICATION NP-COMP NYSDEC
DATE OF COLLECTION 05/14/99 TAGM 4046
DILUTION FACTOR 5 APPENDIX A
PERCENT SOLIDS 94% CRITERIA
UNITS (ug/kg) (ug/kg)
Dichlorodifluoromethane U ----
Chloromethane U ----
Vinyl Chloride U 200
Bromomethane U ----
Chloroethane U 1900
Trichlorofluoromethane U ----
1,1-Dichloroethene U 400
Carbon Disulfide U 2700
lodomethane U ----
Acetone 180 200
Methylene Chloride U 100
trans-1,2-Dichloroethene U 300
1,1-Dichloroethane U 200
Vinyl Acetate U ----
2,2-Dichloropropane U ----
cis-1,2-Dichloroethene U ----
Methyl Ethyl Ketone 260 ----
Bromochloromethane U ----
Chloroform U 300
1,1,1-Trichloroethane U 800
Carbon Tetrachloride U 600
1,1-Dichloropropene U ----
Benzene U 60
1,2-Dichloroethane U 100
Trichloroethene U 700
1,2-Dichloropropane U ----
Dibromomethane U ----
Bromodichloromethane U ----
2-Chloroethyl Vinyl Ether U ----
cis-1,3-Dichloropropene U ----
4-Methyl-2-pentanone U 1000
Toluene U 1500
trans-1,3-Dichloropropene U ----
1,1,2-Trichloroethane U ----
Tetrachloroethene U 1400
1,3-Dichloro ro ane U 300
SOUTHVOL.WK4/mr 1 of 2 05/26/99
TABLE 2 (continued) •
SOUTHOLD LANDFILL
GLASS SAND SAMPLING RESULTS
VOLATILE ORGANIC COMPOUNDS
SAMPLE IDENTIFICATION NP-COMP NYSDEC
DATE OF COLLECTION 05/14/99 TAGM 4046
DILUTION FACTOR 5 APPENDIX A
PERCENT SOLIDS 94% CRITERIA
UNITS (ug/kg) (ug/kg)
2-Hexanone U
Dibromochloromethane U ____
1,2-Dibromoethane U ____
Chlorobenzene U 1700
1,1,1,2-Tetrachloroethane U -___
Ethylbenzene U 5500
Xylene (total) U 1200
Styrene U ____
Bromoform U _--_
Isopropylbenzene U -___
Bromobenzene U _---
1,1,2,2-Tetrachloroethane U 600
1,2,3-Trichloropropane U 400
n-Propylbenzene U _---
2-Chlorotoluene U ____
4-Chlorotoluene U ____
1,3,5-Trimethylbenzene U ____
tert-Butylbenzene U ____
1,2,4-Trimethylbenzene U -___
sec-Butylbenzene U ----
1,3-Dichlorobenzene U 1600
4-Isopropyltoluene U ----
1,4-Dichlorobenzene 110 8500
1,2-Dichlorobenzene U 7900
n-Butylbenzene U _-__
1.2-Dibromo-3-chloropropane U ----
1,2,4-Tdchlorobenzene U 3400
Hexachlorobutadiene U ___
1,2,3-Trichoorobenzene U ----
MTBE U ----
Naphthalene 59 13000
TOTAL VOCs 609 10000
Qualifiers:
U: Compound analyzed for but not detected.
Notes:
----: Not established
SOUTWOLAM/mr 2 of 2 05/26/99
0 TABLE 3 •
SOUTHOLD LANDFILL
GLASS SAND SAMPLING RESULTS
SEMIVOLATILE ORGANIC COMPOUNDS
SAMPLE IDENTIFICATION NP-COMP NYSDEC
DATE OF COLLECTION 05/14/99 TAGM 4046
DILUTION FACTOR 1 APPENDIX A
PERCENT SOLIDS 94% CRITERIA
UNITS (ug/kg) (ug/kg)
Phenol 1500 J 30 or MDL
bis(2-Chloroethyl)ether u ----
2-Chlorophenol U 800
1,3-Dichlorobenzene U 1600
1,4-Dichlorobenzene 740 J 8500
1,2-Dichlorobenzene U 7900
2-Methylphenol U 100 or MDL
2,2'-oxybis(1-Chloropropane) U ----
4-Methylphenol U 900
N-Nitroso-di-n-propylamine U ----
Hexachloroethane U ----
Nitrobenzene U 200 or MDL
Isophorone 370 J 4400
2-Nitrophenol U 330 or MDL
2,4-Dimethylphenol U ----
bis(2-Chloroethoxy)methane U ----
2,4-Dichlorophenol U 400
1,2,4-Tdchlorobenzene U 3400
Naphthalene U 13000
4-Chloroaniiine U 220 or MDL
Hexachlorobutadiene U ----
4-Chloro-3-methylphenol U 240 or MDL
2-Methylnaphthalene U 36400
Hexachlorocyclopentadiene U ----
2,4,6-Trichlorophenol U ---
2,4,5-Trichlorophenol U 100
2-Chloronaphthalene U ----
2-Nitroaniline U 430 or MDL
Dimethylphthalate U 2000
Acenaphthylene U 41000
2,6-Dinitrotoluene U 1000
3-Nitroaniline U 500 or MDL
Acenaphthene U 50000
2,4-Dinitrophenol U 200 or MDL
4-Nitrophenol U 100 or MDL
SOUTSEMI.WK4/mr Page 1 of 2 05/26/99
ORABLE 3 (continued) •
SOUTHOLD LANDFILL
GLASS SAND SAMPLING RESULTS
SEMIVOLATILE ORGANIC COMPOUNDS
SAMPLE IDENTIFICATION NP-COMP NYSDEC
DATE OF COLLECTION 05/14/99 TAGM 4046
DILUTION FACTOR 1 APPENDIX A
PERCENT SOLIDS 94% CRITERIA
UNITS (ug/kg) (ug/kg)
Dibenzofuran U 6200
2,4-Dinitrotoluene U ----
Diethylphthalate U 7100
Fluorene U ----
4-Chlorophenyl-phenylether U ----
4-Nitroaniline U ----
4,6-D initro-2-methyl phenol U ----
N-Nitrosodiphenylamine U ----
4-Bromophenyl-phenylether U ----
Hexachlorobenzene U 410
Pentachlorophenol U 1000 or MDL
Phenanthrene U 50000
Anthracene U 50000
Di-n-butylphthalate 960 J 8100
Carbazole U ----
Fluoranthene U 50000
Pyrene U 50000
Butylbenzylphthalate 10000 50000
3,3'-Dichlorobenzidine U ----
Benzo(a)anthracene U 224 or MDL
Chrysene U 400
3,3'-Dichlorobenzidine U ----
bis(2-Ethylhexyl)phthalate 6300 50000
Di-n-octylphthalate U 50000
Benzo(b)fluoranthene U 1100
Benzo(k)fluoranthene U 1100
Benzo(a)pyrene U 61 or MDL
Indeno(1,2,3-cd)pyrene U 3200
Dibenzo(a,h)anthracene U 14 or MDL
Benzo(g,h,i)perylene U 50000
Qualifiers:
U: Compound analyzed for but not detected.
J: Result found below CRDL, value estimated.
Notes:
----: Not established. 0: Value exceeds the
MDL: Method Detection Limit. NYSDEC TAGM Criteria.
SOUTSEMI.WKMmr Page 2 of 2 05/26/99
TABLE 4
SOUTHOLD LANDFILL
GLASS SAND SAMPLING RESULTS
PCBs
SAMPLE IDENTIFICATION NP-COMP NYSDEC
DATE OF COLLECTION 05/14/99 TAGM 4046
DILUTION 1 APPENDIX A
PERCENT SOLIDS 94% CRITERIA
UNITS (ug/kg) (ug/kg)
Aroclor-1016 U ----
Aroclor-1221 U ---- 40
Aroclor-1232 U ---
Aroclor-1242 U ----
Aroclor-1248 U ----
Aroclor-1254 U ----
Aroclor-1260 U --
TOTAL PCBs 0 10000*
Qualifiers:
U: Compound analyzed for but not detected.
Notes:
—: Not established.
NA: Information not available.
* : Criteria is for total PCBs in subsurface soil. •
S0UPCPES.WK4/mr 05/26/99
~ TABLE 5
SOUTHOLD LANDFILL
GLASS SAND SAMPLING RESULTS
PESTICIDES AND HERBICIDES
SAMPLE IDENTIFICATION NP-COMP NYSDEC
DATE OF COLLECTION 05/14/99 TAGM 4046
DILUTION FACTOR 1 APPENDIX A
PERCENT SOLIDS 94% CRITERIA
UNITS (ug/kg) (ug/kg)
Pesticides
Endrin Ketone U ----
alpha-BHC U 110
gamma-BHC (Lindane) U 60
Heptachlor U 100
Aldrin U 41
beta-BHC 5.6 P 200
delta-BHC U 300
Heptachlor Epoxide U 20
Endosulfan I U 900
4,4'-DDE U 2100
Dieldrin U 44
Endrin U 100
4,4'-DDD U 2900
Endosulfan II U 900
4,4'-DDT U 2100
Endrin Aldehyde U ----
Methoxychlor U ----
Endosulfan Sulfate 2.8 1000
Toxaphene U ----
alpha-Chlordane 2.5 540
gamma-Chlordane 4.1 540
Herbicides
2,4-D U 500
2,4,5-TP Silvex U 700
Qualifiers:
U: Compound analyzed for but not detected.
P: Concentration estimated, possibly biased low since
primary and confirmation column concentrations had a
%D >25%, lower value reported.
Notes:
----: Not established
SOUPCPES.WK4/mr 05/26/99
v
hDvirka
and
CONSULTING Bartilucci ENGINEERS
330 Crossways Park Drive,Woodbury, New York, 11797-2015
516-364-9890 ■ 718-460-3634 n Fax:516-364-9045
e-mail: db-eng*woddnet.att.net
May 11, 1999
Ernest Lampro, Jr.
New York State Department of Environmental Conservation
Division of Solid& Hazardous Materials, Region One
Building 40—SUNY
Stony Brook, New York 11971
Re: Southold Landfill
Glass Sand Sampling
D&B No. 1314-F2
Dear Mr. Lampro:
In accordance with your request, presented below is a proposed plan for obtaining a
representative sample and analyzing the glass sand presently stockpiled at the Town of Southold
Landfill. The approach to sampling the stockpile is based on the guidance presented in the
USEPA document, "Superfund Program Representative Sampling Guidance, Volume 4: Waste"
published by the Office of Solid Waste and Emergency Response (Interim Final Dated:
December 1995).
Four (4) grab samples will be collected from the stockpile. One (1) grab sample will be collected
from each side (north, east, south and west) of the stockpile. The grab samples will be collected
at a depth of approximately 3 feet from the surface of the pile. A shovel will be used to dig
approximately 2.5 feet into the pile. A disposable plastic scoop will be used to dig the last
0.5 feet into the pile and collect the samples.
The grab samples will be composited into a single representative sample at the analytical
laboratory. The composite sample will be analyzed for target analyte list (metals) parameters.
The laboratory used will be a laboratory that has been certified by the NYSDOH under the
environmental laboratory approval program (ELAP). A laboratory turnaround time of one-week
will be requested and the results will be forwarded to the NYSDEC upon receipt.
The sampling will be performed as soon as we receive your approval of the procedures described
above.
A DIVISION OF WILLIAM F.COSULICH ASSOCIATES,P.C.
OVIAKA AND BAATILUCCI
Ernest Lampro,Jr. Page Two
New York State Department of Environmental Conservation
Division of Solid& Hazardous Materials, Region One
May 11, 1999
If you have any questions regarding this matter or require additional information, please do not
hesitate to contact me.
Very truly yours,
Thomas F. Maher, P.E.
Vice President
TFM/DSG(tp)/ld
cc: Jean Cochran, Supervisor, Town of Southold
Alice Hussie, Town of Southold
James Bunchuck, Town of Southold
David Glass, Dvirka and Bartilucci
♦1314rrFM99-14.LTR(RO1)
e
d1Dvirka
and
0 Bartilucci
CONSULTING ENGINEERS
330 Crossways Park Drive,Woodbury, New York, 11797-2015
516-3649890 • 718-460-3634 ■ Fax:516-364-9045
e-mail: db-eng0worldnet.att.net
February 1, 1999
Ernest Lampro,Jr.
New York State Department of Environmental Conservation
Division of Solid&Hazardous Materials, Region One
Building 40—SUNY
Stony Brook,New York 11971
Re: Southold Landfill
Filling of Former Scavenger Waste Lagoons and
Scrap Metal Recovery
D&B No. 1314-F2
Dear Mr.Lampro:
On behalf of the Town of Southold we are writing to inform you that the Town intends to begin filling in
the former scavenger waste lagoons at the landfill. The glass sand being provided to the Town by Waste
Management as approved by NYSDEC will be used. The filling will be conducted in accordance with the
recommendations presented in the enclosed compaction test report prepared by Tectonic Engineering
Consultants (TEC).
The existing (unburied) construction and demolition (C&D) material at the landfill also will be used in
conjunction with the glass sand to fill the lagoons. Recommendations, prepared by TEC, for use of the
C&D in filling in the lagoons will be followed. TEC's recommendations are presented in the enclosed
letter dated January 22, 1999.
In addition, the Town intends to begin recovering the metal scrap buried in the northwest corner of the
landfill. The operation will involve excavating and screening the metal scrap. The screened scrap will be
conveyed directly to containers being provided by Franza Universal of Farmingdale, New York. The
containerized metal scrap will be transported off site for recycling by Franza Universal. The resulting
screened soil will be used to cover the excavation at the end of each day.
If you have any questions regarding this matter or require additional information,please do not hesitate to
contact me.
rslly yo
tur ,,
Thomas F.Maher,PE
Vice President
TFM/DSG/bl
cc: Jean Cochran, Supervisor,Town of Southold
Alice Hussie,Town of Southold
James Bunchuck,Town of Southold
David Glass, Dvirka and Bartilucci
♦1314nFM99-0l.ltr(R01)
A DIVISION OF WILLIAM F.COSULICH ASSOCIATES,P.C.
REGIONAL OFFICES
T���® p dQ� ENGINEERING Latham,New York 518.783-1630
B I tl Auburn,Massachusetts 508.832-7146
CONSULTANTS P.C. west Chester.Ohio 513.759-9500
P.O.Box 447,615 Route 32 Fax No.914-928-9211
Highland Mills, New York 10930 914-928-6531
Mr. Thomas F. Maher, P.E.
Vice President
Dvirka and Bartilucci Consulting Engineers
330 Crossways Park Drive
Woodbury, New York, 11797-2015
January 19, 1999
RE: W.O. #2142.04
SOUTHOLD LANDFILL CLOSURE
LANDFILL COVER SYSTEM MATERIAL
FIELD AND LABORATORY TEST RESULTS
SOUTHOLD, NEW YORK
Dear Mr. Maher:
In accordance with our proposal dated October 23, 1998, Tectonic Engineering has
performed field and laboratory testing of the glass sand material. As we understand it,
the glass sand will be used as a bulk fill to raise the existing landfill waste mass grades
to the final subgrade elevations of the landfill cap. The following presents our
investigation, findings, and recommendations for use of the glass sand material for this
purpose.
1.0 LABORATORY TESTING AND FINDINGS
During our December 29, 1998 field visit, one bulk sample was obtained from the glass
sand material stockpile to perform one test for grain size, moisture content and
moisture-density relations. The maximum dry density (MDD) and optimum moisture
content (OMC) was determined from the moisture density relations test commonly
referred to as the Modified Proctor (ASTM D 1557). The tests were reported on
January 6, 1999 (attached). Also attached are the results of previous testing reported
on June 17 and 22, 1998, which were performed for grain size, moisture content and
MDD and OMC using the Standard Proctor (ASTM D 698) method. The change in
testing methodology from ASTM D 698 to ASTM D 1557 was made to: 1) obtain a MDD
and OMC that is more representative of the level of compactive effort provided by
modern construction equipment; and 2) provide a reference that is consistent with
general landfill engineering practice at this time.
CIVIL-GE-C-TECHNICAL- STRUCTURAL =';G;NE=RS
NEENG
TECTONIC 'SULTANTSPC
Mr. Thomas F. Maher, P.E. 2 January 19, 1999
The recent material grain size gradation reported on January 6, 1999 was found to be
very similar to the gradation from previous testing reported on June 17, 1998. The
material is equivalent to a coarse to fine sand and is very angular to sharp. The
moisture content of the recent and previous grain size tests were found to vary. This
can be expected due to weather conditions, seasonal changes, length of time the
material was stockpiled, and where the sample was taken from within the stockpile. In
addition, during the in-place field testing, bag samples were collected to test for
laboratory moisture contents to verify field moisture contents obtained by the nuclear
gauge. The comparison found that the actual laboratory moisture is about 2% higher
than the field moisture. As a result, field values should be adjusted upwards about 2%
to obtain the actual moisture. This should be noted for adjustments during the CQA
testing of construction earthwork.
According to ASTM D 1557, the laboratory testing found that the glass sand has a MDD
of 115.5 pcf at an OMC of 9.0%. Note that previous testing according to ASTM D 698
found a MDD of 112.0 pd at 12.0%. The difference in MDD is typical (within about 5 pcf
or 5%), which reflects the higher energy level used to compact soil in the lab using the
methodology of ASTM D 1557. These MDD's and OMC's are within a typical range for
sand.
1.0 FIELD INVESTIGATION AND FINDINGS
On December 29, 1998, a representative of Tectonic Engineering visited the Southold
Landfill site and directed the Town's forces for the construction of a test pad to
determine the compaction characteristics of the glass sand material. Two wedge
shaped lifts of the material were constructed. The first was roughly 30' by 20' and
ranged in thickness from about 2" to 14". The second lift was roughly 25' by 20' and,
varied from 6" to over 24" in thickness. Each pad was constructed by using a front-end
loader to dump glass sand piles that were shaped and compacted into lifts using arr
Fiat-Alice FD30B bulldozer. The bulldozer compacted the glass sand by tracking over
the material in two passes.
A nuclear density gauge was then used to test the in-place density of the material in
locations where the lift thickness was found to be 6, 8, 10, 12, 18, and 24 inches.- Two
tests were taken in each location by rotating the nuclear gauge 180 degrees. In
addition, two sets of tests were performed at different water contents for the 12" lift
thickness to evaluate the compaction for a water content closer to the OMC.
The June 22, 1998 standard proctor test was used to guide and evaluate whether
acceptable compaction was being achieved during the field testing. The actual in-place
density values obtained were then compared to both the standard proctor and modified
. s �
IN
TECTONIC ENG�JN'SULTANGSPC.
Mr. Thomas F. Maher, P.E. 3 January 19, 1999
proctor MDD as shown in the attached ""Field Testing In-Place Density Report"
summary sheet. Note that the compaction values achieved in the field are calculated by
dividing the measured in—place dry density by the MDD.
The testing indicates that the material readily compacts using standard construction
equipment, such as the bulldozer provided by the town. It also indicated that the
material is capable of being compacted to the required degree even when the moisture
content is low, in the adjusted (2% upwards) range of 5% to 7%, which is 20/6 to 4%
below the ASTM D 1557 OMC of 9.0%. Normally, material specifications require
material to be within about 2% of OMC to achieve the required compaction and increase
the relative ease of material placement. The field testing shows the glass sand can
achieve a minimum in-place density of about 90% relative to ASTM D 1557 for lifts in
the range of 8 to 18 inches at below optimum moisture contents. In summary, the glass
sand achieved an acceptable level of compaction with a reasonable level of effort.
It should be noted that when working in close proximity to the glass sand material at a
low moisture content, the dust from the glass was found to be an eye irritant.
3.0 RECOMMENDATIONS
Based on the preceding findings, we recommend that the following criteria be followed
for placement and use of the glass sand:
Glass Sand as Bulk Fill Material Below Landfill Cag
The following recommendations are for general use of the glass sand as a bulk fill:
•• The material should have a minimum specified in-place density of 90% of the
maximum dry density as determined in accordance with ASTM D 1557.
• The material should be placed with a moisture content within 2% of the optimum
moisture content.
• The material should be placed in maximum compacted lifts of 9 inches.
• The glass sand should be separated from geomembrane liners by a minimum of
6 inches of suitable soil or protective fabric to prevent puncturing as a result of
contact with the sharp edges of the glass particles.
• We recommend that a dust control plan be prepared that anticipates the potential
need for low-level eye and respiratory protection should the dust not be
ENGINEERING
TECTONIC CONSULTANTS P C.
Mr. Thomas F. Maher, P.E. 4 January 19, 1999
suppressed through moisture control measures. Moisture control would likely be
achieved by maintaining the material within 2% of the optimum moisture content,
but the criteria for implementing personnel protection should be based on field
conditions at the time of construction.
Glass Sand as Bulk Fill Material in Lagoons
The following additional recommendations address the placement of glass sand
in the lagoons only by the Town's municipal forces:
• The soil should be placed in maximum compacted lifts of 9 inches.
Providing the moisture content remains very close to the moisture contents
found for the stockpiled material we tested, the soil can be placed with no
adjustment of moisture.
• The compaction effort must be greater than or equal to two tracking passes
over the complete lift surface of the glass sand using equipment that exerts a
ground pressure greater than or equal to the Town's Fiat-Alice FD30B
bulldozer.
Please call me if you have questions regarding this report.
Sincerely,
TECTONIC ENGINEERING CONSULTANTS, P.C.
/,7 7
Peter T. Sutherland, P.E.
Senior Geotechnical Engineer
Attach.
PTS/c:lprojects\southold\2142.04GIassrep.doc
OJECT No.2142.01 DATE: 1/6/99 GRAIN SIZE ANALYSIS
TECTONIC PROJECT: Southold Landfill
ENGINEERING CONSULTANTS P.C.
LOCATION: Southold, N.Y. i, soURCE:GIass Mat. From Waste Managemea
U.S.SIEVE OPENING IN INCHES U.S. SIEVE NUMBERS I HYDROMETER
12 6 4 3 2 1.5 13,L41/23/8 3 4 6 810 1416 '0 30 40 50 70 100140 200
l00 I El 11 11 1 111111
90 1
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GRAIN SIZE IN MILLIMETERS
GRAVEL SAND
COBBLESi SILT OR CLAY
coarse fine coarse I medium � fine
Specimen Identification Classification MC% LL PL PI Cc Cu
• BS-MCI Gy c-f GLASS, trace Silt 1 6 1.14 low
I
i I
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Specimen Identification D 100 D60 D30 D 10 %Gravel %Sand ! %Silt %Clay
• BS-MC1 19.00 1.45 0.480 0.1400 9.0 85.5 5.5
' I
I
` OJECT No.2142.01 DATE: 1/6/99W COMPACTION TEST
TECTONIC ! PROJECT: Southold Landfill
ENGINEERING CONSULTANTS P.C.
LOCATION: Southold, N.Y. 'i souttcE:Glass Mat. From Waste Manageme
150
I
145
I
j Specimen Identification BS-MCI
140 Description of Material Gy c-f GLASS.trace Sift
Test Method ASTM D1557/A
135
D
R i TEST RESULTS
Y
D 130 Maximum Dry Density 115.5 PCF
E i Optimum Water Content 9.0 °b
N
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P LL PL PI
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CURVES OF 100% SATURATION
P FOR SPECIFIC GRAVITY EQUAL TO:
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WATER CONTENT(Percent Dry Weight)
MOISTURE-DENSITY RELATIONSHIP
GRAIN SIZE AN
fie/ PROJECT: Southold Landfill
SOURCE-Glass Mat. From Waste Managemer
LOCATION: Southold,11N.Y.-
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IECT No.2142.01 DATE: 6/2219 COMPACTION TEST
TECl01VIC PROJECT: Southold Landfill
ENGINEERING CONSULTANTS P.C. LOCATION: Southold, N.Y. souRCE:Glass Mat. From Waste Managemei
150 Fl�
145
Specimen Identification BS-4
Description of Material Gy c-f GLASS. trace Silt
140
Test Method ASTM D698/A
135
D TEST RESULTS
R
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D 130Maximum Dry Density 112.0 PCF
I LL E Optimum Water Content 12.0
N
S
T ATTERBERG LIMITS
y 125
P LL PL P1
o % % %
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a 120 CURVES OF 100% SATURATION
s FOR SPECIFIC GRAVITY EQUAL TO:
e 2.80
r
115 ---------- 2.70
C
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105
100
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900 5 10 15 20 25 30
WA'T'ER CONTENT(Percent Dry Wctght)
MOISTURE-DENSITY RELATIONSHIP
TECTONIC ENGINEERING P.C.
DETERMINATION OF WATER (MOISTURE) CONTENT OF SOIL
ASTM D4959
....................................................
TEC W.O. 214114
:.:.
PROJECT: TESTED BY: .-X...-1-.-
.
Y _1-
: ..........
DATE SAMPLED. CHECKED BY::10,
DATE TESTED. :: 12 ?/9€ «:..... ...;
Sample I1w4 Mme'
Container#
Wt. of Container164 4 190 9. 27: 27.
Wt. of Container+Wet Soil 347;4 339:fi 14.2 ..
1.45: <287.4
Wt. of Container+ Dry Soil 299;4 «321.7 X44 .: 139 . Z78. .
Wt. of Water 8 11.9 5.2 6.3 9.4
Wt. of Dry Soil 135 236.8 121.3 111.2 187.2
Water Content 5.93% 5.03% 4.29% 5.67% 5.02%
Sample I.D.1 VISUAL DESCRITPION
MS-1 ND, LOC. 1/1 A BWN/GN SAND, trace gravel, trace silt
MS-2 ND, LOC. 2 BWN/GN SAND,trace gravel, trace silt
...... ...... ....
MS-3 BWN/GN SAND,trace gravel,trace silt
.... .. ..........
MS-4 ND, LOC. 3A BWN/GN SAND, trace gravel, trace silt
MS-6 ND, LOC. 11 A BWN/GN SAND, trace gravel, trace silt
TECTONIC ENGINEERING P.C.
DETERMINATION OF WATER (MOISTURE) CONTENT OF SOIL
ASTM D4959
TEC W O 2. 42104
PROJECT: Scarath .Landfiti TESTED BY Imo:
DATE SAMPLED 12120 ;..:..: ...... CHECKED BY: .
DATE TESTED t2101i ::... .... ::
Sample I D hi( -5
MS 7! .
Container# I` .
Wt. of Container 27:3 28.5 ;!
Wt. of Container+ Wet Soil 124:6 15.7
Wt. of Container+ Dry Soil 1 tig 129 S..:....
Wt. of Water 5.8 5.8
Wt. of Dry Soil 91.5 101.4
Water Content 6.34% 5.72%1 1
Sample I.D. VISUAL DESCRITPION
MS-5 ND, LOC. 6 BWN/GN SAND, trace gravel, trace silt
MS-7 ND, LOC. 14 A BWN/GN SAND, trace gravel, trace silt
SOUTHOLD LANDFILL
W.O.#2142.04
FIELD TESTING IN-PLACE DENSITY REPORT
Sample ID MDD OMC Prepared by: PTS
BS-4 112.0 12.0% Date: 1/11/99
BS-MC1 115.5 9.0%
Adjusted BS-4 BS-MCI
Depth Field Field Adjusted %MOD %MOD
Test Lift Source Soil Moisture') Moisture Test Test Standard Modified
No Lift# Depth Rod ID pcf % (pcf) DO(pcf) DD(pcf) Proctor Proctor
1 1 10 8 BS-4/BS-MCI 2.9 2.7% 4.9 107.0 105.0 93.7% 90.9%
1A 1 10 8 BS-4/BS-MC1 2.9 2.8% 4.9 105.4 103.4 92.3% 89.5%
2 1 10 8 BS-4/BS-MC1 3.7 3.5% 5.7 106.8 104.8 93.6% 90.7%
2A 1 10 8 BS-4/BS-MC1 3.7 3.4% 5.7 108.3 106.3 94.9% 92.0%
3 1 8 6 BS-4BS-MC1 3.7 3.5% 5.7 104.5 102.5 91.5% 88.8%
3A 1 8 6 BS-4/BS-MC1 2.6 2.4% 4.6 106.6 104.6 93.4% 90.5%
4 1 8 6 BS-4/BS-MCI 4.2 3.9% 6.2 106.6 104.6 93.4% 90.6%
4A 1 8 6 BS-4/BS-MCI 3.4 32% 5.4 105.8 103.8 92.7% 89.9%
5 1 6 3 BS-41BS-MC1 3.4 32% 5.4 106.3 104.3 93.1% 90.3%
5A 1 6 3 BS-4/BS-MCI 4.0 3.8% 6.0 105.5 103.5 92.4% 89.6%
6 1 6 3 BS-4/BS-MC1 5.3 5.1% 7.3 103.3 101.4 90.5% 87.8%
6A 1 6 3 BS-4/BS-MCI 4.2 4.0% 6.2 104.7 102.7 91.7% 88.9%
7 1 12 10 BS-4/BS-MC1 4.0 3.8% 6.0 105.9 103.9 92.8% 90.0%
7A 1 12 10 BS-4/BS-MCI 2.9 2.7% 4.9 107.3 105.3 94.0% 91.1%
8 1 12 10 BS-4/BS-MC1 3.7 3.4% 5.7 107.7 105.7 94.3% 91.5%
8A 1 12 10 BS-4BS-MC1 4.5 4.2% 6.5 107.8 105.8 94.4% 91.6%
9 2 14 12 BS-4/BS-MCI 9.0 8.5% 11.0 106.1 104.2 93.0% 90.2%
9A 2 14 12 BS-4BS-MC1 8.7 8.1% 10.7 108.0 106.0 94.7% 91.8%
10 2 12 12 BS-4/BS-MCI 4.8 4.3% 6.8 111.8 109.7 98.0% 95.0%
10A 2 12 12 BS-4/BS-MCI 6.1 5.5% 8.1 111.6 109.5 97.8% 94.8%
11 2 18 12 BS-4/BS-MCI 3.2 2.9% 5.2 109.3 107.2 95.7% 92.8%
11A 2 18 12 BS-4/BS-MC1 2.9 2.7% 4.9 107.0 105.0 93.7% 90.9%
12 2 18 12 BS-4/BS-MCI 3.4 3.1% 5.4 111.0 108.9 97.2% 94.3%
12A 2 18 12 BS-4/BS-MCI 3.7 3.4% 5.7 109.0 106.9 95.5% 92.6%
13 2 24 12 BS-4/BS-MCI 5.8 5.4% 7.8 107.3 105.3 94.0% 91.2%
13A 2 24, 12 BS-4/BS-MCI 4.2 4.0% 6.2 105.7 103.7 92.6% 89.8%
14 2 24 12 BS-4/BS-MCI 5.0 4.8% 7.0 103.5 101.6 90.7% 87.9%
14A 2 24 12 BS-4/BS-MC1 5.6 5.4% 7.6 104.1 102.2 91.2% 88.5%
Note:(1)Field moisture contents should be adjusted upwards approximately 2%to obtain true moisture contents.
REGIONAL OFFICES
^' '+ �► Latham,New York 518-783-1630
ENGINEERING
l` Auburn,Massachusetts 508.832-7146
CONSULTANTS PC. west Chester,Ohio 513.759-9500
P.O.Box 447,615 Route 32
Fax No.914-928-9211
Highland Mills, New York 10930 914-928-6531
Dvirka and Bartilucci Consulting Engineers
330 Crossways Park Drive
Woodbury, New York, 11797-2015
Attention: Mr. Thomas F. Maher, P.E.
January 22, 1999
RE: W.O. #2142.04
SOUTHOLD LANDFILL CLOSURE
CONSTRUCTION AND DEMOLITION DEBRIS
LAGOON FILL
SOUTHOLD, NEW YORK
Dear Mr. Maher:
As requested, Tectonic Engineering has reviewed in concept the proposed use of
residential construction and demolition debris (C&D) as bulk fill for the landfill lagoon.
The lagoon is located in the northwest comer of the landfill along the landfill "footprint"
edge. The lagoon is about 400 feet long, an average of about 120 feet wide, and about
25 feet deep.
The use of the C&D for lagoon fill is based on the following technical assumptions:
1. The C&D is of a mixed character, i.e., composed of various materials
resulting from residential yard work, earthwork, and building demolition
and construction.
2. The total volume of C&D stockpiled on site is about 1,000 CY.
3. Based on our review of the preliminary grading plans for the Southold
Landfill closure provided to our office by Dvirka and Bartilucci, the
proposed maximum fill over the top of the lagoon surface is about 10 feet.
The recommendations for use of the C&D in the lagoon are as follows:
• The material should be mixed before being placed to the greatest degree
practicable.
• The C&D should be placed in 8-inch compacted lifts.
• Compaction of each lift should be performed with at least four passes over
the complete lift surface using the Town's Fiat-Alice FD30B bulldozer or
compaction equipment with an equivalent or greater ground pressure.
CIVIL-GEOTECHNICAL-STRUCTURAL ENGINEERS
. s �
-r• r i+. - y ENG+NEEPING
� C%S;L-;NTS
Mr. Thomas F. Maher, P.E. 2 January 22, 1999
• The C&D should be placed in alternating lifts with the glass sand or other
acceptable bulk fill material. As discussed in our letter dated January 19,
1999, the glass sand should be placed in compacted lifts of 9 inches and
compaction of the glass sand should be performed with at least two passes of
the bulldozer.
• No significant quantities of materials that create hydrogen sulfide, such as
gypsum board, should be landfilled.
• The C&D should only be deposited at an elevation that is at least 5 feet above
the seasonal high groundwater level.
In summary, if the above assumptions and recommendations are followed, the C&D
should be acceptable for use as fill in the lagoons.
Please call me if you have questions.
Sincerely,
TECTONIC ENGINEERING CONSULTANTS, P.C.
/ZZ,
Peter T. Sutherland, P.E.
Senior Geotechnical Engineer
PTS/cAprojects\.southold\2142.04 C&D rep.doc
JUN- 15-99 11 07 FROM- 0 ID- 48675
PACF. 1/3
PRIVILEGE AND CONFIDENTIALITY NOTICE
The information .in this fax is intended for the named
recipients only. It may contain privilig,W and confidential
matter. If you have received this-fax in error,please notify
virka us. immediat �+ OY a collect telephone' Gall to (816
and 384-E�A0 a return the original to the render.0 mai(
We will relrr Wmo you for po$tape. Do not diseidss the
Bartiluml 0011460 to-drtyorim. Thank you.
d[b cOWLTING ENaINIEERS
330 Crossways Park Drive,Woodptny,Now York, 11797.201.6
618.364-9890 a Fax:316.38¢9W
D&B FAX NO: (516) 364-9045 DATE:
1
COMPANY NAME
ATTENTION: J11,
"
FAX NO.: 7%"��-,-74057b
FROM: --�
SUBJECT: ��J�-�- .: JOBS:
NO. OF PAGES:
(including cover sheet)
MESSAGE: �-
THANK YOU;
A DIVISION OF WILLIAM F.COWLICN A6800IATES,P.C.
JUN- 15-99 11 :09 FROM- 1D: 0649675 PAGE 2/3
-DRAFT-
[Town of Southold Letterhead]
- Date -
Robert Boorum
Waste Management of New York, Inc, - - -
75 Thomas Street
Brooklyn,New York 11222
Re: Class Sand
Town of Southold Landfill
Dear Mr. Boorum:
I am forwarding the enclosed letter from the New York State Department of Environmental.
Conservation (NYSDEC) for.your information. As you can sec, the letter, requires chemical
analysis of every 10,000 to 12;000 cubic-yards-.of the glass sand RE&to.delivery to the Southold
Landfill.
As a result; I am requesting that you provide us with the results of chemical analysis of each
10,000cubic yards of glass°sand that you intendto deliver to the landfill: Toallow for Town
review;please submit the results to this:office at least one week prior to initiating delivery.of the
material that each sample was collected from. Each sample should be:analyzed for.the full target:
compound list and target.analyte list parameters and cyanide.
If you have any questions please contact me at(51.6) 734-7685.
Sincerely,
James Bunchuck
Solid Waste Coordinator
JB/DSGt/ld
cc: Supervisor Cochran
T. Maher(D&B)
D. Glass (D&B)
•1114/M1sc99-011TR(Ra)
JUN-IS-SS 11 : 09 FROM: ID: s964867S PACE 3/3
New York State Department of Environmental Conservation
Division of Solid & Hazardous Materiels, Flegion One
Building 40 . SUNY, Stony Brook, New York 11790-2356
Rhone: (616) 444-0376 FAX: (616) 444.0231 PCON11
Commissioner
June 4, 1999
The Honorable Jean W. Cochran
Supervisor Town of Southold
Town Hail
59095 Main Road
Southold,New York 11971
Dear Supervisor Cochran:
The New York State Department of Environmental Conservation (Department) has received and
reviewed the analytical results from the May 14, 1999 sampling of the-glass sand material currently on the
Southold landfill. Both the"old pile"and the"new pile"are acceptable for use as grading material beneath
the liner of the landfill.
The Department has approved in an August 12,.1998.letter,the use of Waste Management generated
glass sand beneath the liner for grading of the Southold.Landfill. At that time certain restrictions were placed
on-the acceptance 404 use of the material. Howeverjhe Department;at that tinw,did not require periodic
asariysis of the material, To correct this and prevent any future occuftnoe of the events which lod to the
treed to perfoim the May 14 sampling;the Department will require a,full.imaiysis of the'Slass$anti material
for eVery.10,000- 12;000 cubic yards brought to the Southold landfill. The analytical results should be
reviewed by the Town of Southold and the Department prior to any of the.material being brought to the
landfill.
If there are any questions please contact meat 516-444-0388.
Sincerely,
Ernest Lampro Jr.
Environmental Engineer I
ce: Alice Hussie,Town of Southold
Gregory Yakaboski;Town of Southold
James Bunahuok,Town of Southold
Melissa Treers,NYSAEC,Albany •-'
Tom Maher,D&B
David Glass;D&B
file: 52S17
7
MAY-11-99 00: 50 FROM: 1130 3649045 PAGE 1,'3
PRIVILEGE AND CONFIDENTIALITY NOTICE
The information in this fax is intended for the named
recipients only. It may contain privileged and confidential
matter. If you have received this fax In error, please notify
Dvirka us immediately by a collect telephone call to (516)
and 364-9890 and return the original to the sender by mail.
0 Bartilucci I will reimburse you for postage. Do not disclose the
contents to anyone. Thank-you.
d1bCONSULTING ENGINEERS
330 Crossways Park Drive,Woodbury, New York, 11797-2015
516-364-9690 9 Fax:516-364-9045
D&B FAX NO: (516) 364-9045 DATE: ' AVT
40
44'
COMPANY NAME . 40'1
ATTENTION: V JIM
FAX NO.:
FROM: I�l�-lIG alb
SUBJECT: f JOB#:
NO. OF PAGES:
(including cover sheet)
MESSAGE:
Ve, VI
GRIP ,�
THANK YOU:
G
A DIVISION OF WILLIAM F.COSULICH ASSOCIATES,P.C.
MAY-11-99 09: 51 FROM: I0- 0649045 PAGE 2%3
-DRAFT-
May 10, 1999 "
Ernest Lampro, Jr.
New York State Department of Environmental Conservation
Division of Solid &Hazardous Materials, Region One
Building 40—SUNY
Stony Brook, New York 11971
Re: Southold Landfill
Glass Sand Sampling
D&B No. 1314-172
Dear Mr. Lampro:
In accordance with your request, presented below is a proposed plan for obtaining a "
representative sample and analyzing the glass sand presently stockpiled at the Town of Southold
Landfill. The approach to sampling the stockpile is based on the guidance presented in the
USEPA document, "Superfund Program Representative Sampling Guidance, Volume 4: Waste"
published by the Office of Solid Waste and Emergency Response (Interim Final Dated:
December 1995).
Four(4) grab samples will be collected from the stockpile. One (1) grab sample will be collected
from each side (north, east, south and west) of the stockpile. The grab samples will be collected
at a depth of approximately 3 feet from the surface of the pile. A shovel will be used to dig
approximately 2.5 feet into the pile. A disposable plastic scoop will be used to dig the last
0.5 feet into the pile and collect the samples.
The grab samples will be composited into a single representative sample at the analytical
laboratory. The composite sample will be analyzed for target analyte list (metals) parameters.
The laboratory used will be a laboratory that has been certified by the NYSDOH under the
environmental laboratory approval program (ELAP). A laboratory turnaround time of one-week
will be requested and the results will be forwarded to the NYSDEC upon receipt.
The sampling will be performed as soon as we receive your approval of the procedures described
above.
Or
MAY-11-99 08: 52 FROM: 0 ID: 0649045 PAGE 3/3
Ernest Lampro, Jr. Page Two
New York State Department of Environmental Conservation
Division of Solid & Hazardous Materials, Region One
May 11, 1999
If you have any questions regarding this matter or require additional information, please do not
hesitate to contact me.
Very truly yours,
ry
Thomas F. Maher, P.E.
Vice President
TFM/DSG(tp)/ld
cc: Jean Cochran, Supervisor, Town of Southold
Alice Hussie, Town of Southold
James Bunchuck,Town of Southold
David Glass, Dvirka and Bartilucci
♦1314/TFM99-14.LTR(R01)
tr,
fr:
�r
MAY-27-99 15 : 39 FROM: • IDTS18364S PACE 1/9
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Post-it' FaX NUIe 1 �'''� c,, payis►
To
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Bartilucc� Fa:a FaxR
ENGINEERS
330 Crossways Park Drive,Woodbury,New York,11797.2015
516-364-9690 • 718-460-3634 ■ Fax:516-364-9045
e-mail: &-eng0wortdnet a t.net
May 26, 1999
Ernest Lampro,Jr.
New York State Department of Environmental Conservation
Division of Solid& Hazardous Materials,Region One
Building 40—SUNY
Stony Brook,New York 11971
Re: Southold Landfill
Glass Sand Sampling
D&B No. 1314-F1
Dear Mr. Lampro:
Enclosed please find the results of the analytical testing which you requested for the glass sand at
the Southold Landfill. As you know two piles were sampled on May 14, 1999.
Four grab samples, one from each side, were collected from the pile near the former lagoon (the
"New Pile"). The grab samples were collected at a depth of approximately 3 feet from the
surface of the pile. Since staining and odors were observed, as directed, a portion of one of the
four grab samples was tested for volatile organic compounds(VOCs). In addition,the remainder
of the grab sample tested for VOCs and the other three grab samples were composited by the
laboratory and tested for metals, cyanide, semivolatile organic compounds, PCBs,pesticides and
herbicides.
Two grab samples were collected from the pile near the high voltage electric line tower(the"OId
Pile"). The grab samples were collected at a depth of approximately 3 feet from the surface of
the pile and composited by the laboratory. The composite sample was tested for metals.
On the enclosed tables the results are compared to the recommended soil cleanup objectives in
TAGM 4046 (Determination of Soil Cleanup Objectives and Cleanup Levels). The
concentrations of zinc detected in both samples(i.e., 87 mg/kg and 61 mg/kg)slightly exceed the
TAGM value of 20 mg/kg; however, this is an extremely conservative cleanup level. The
semivolatile organic compound phenol was reported at a concentration of 1,500 ug/kg in the
composite sample collected from the New Pile. This exceeds the cleanup level for phenol of 30
ug/kg; however, the result was qualified by the laboratory as an estimated value since it was
detected below the contract required detection limit. In addition, the total concentration of
semivolatile organic compounds detected in the composite sample from the New Pile is 19,870
ug/kg,which is well below the TAGM criteria of 500,000 ug/kg.
A DIVISION OF WILLIAM F.COSULICH ASSOCIATES.P.C.
MAY-27-99 IS :40 FROM: ID: S163804S PAGE 2/9
OVIRKA ANO BARTILUCCI
Ernest Lampro,Jr. Page Two
New York State Department of Environmental Conservation
Division of Solid&Hazardous Materials, Region One
May 26, 1999
Based on our review of these results, the material is acceptable for the intended use as general
fill/contour grading material to be placed below the gas venting layer and HDPE geomembrane
of the landfill cap. Please contact me at your earliest convenience with your determination so
that the Town can start accepting the glass sand again and complete the effort of filling in the
former lagoon.
If you have any questions regarding this matter or require additional information, please do not
hesitate to contact me.
Very truly yours,
Thomas F.Maher,PE
Vice President
TFFM/DSGt/kd
cc: Jean Cochran,Supervisor,Town of Southold
James Bunchuck,Town of Southold
David Glass,Dvirka and Bartilucci
♦1314/efM"-16JV-Qt01)
TABLE 1 a
SOUTHOLD LANDFILL �
GLASS SAND SAMPLING RESULTS
METALS AND CYANIDE
co
RECOMMENDED EASTERN m
SOIL USA N
CLEANUP BACKGROUND
PERCENT sc)t-ins e UNIMA
a
n
Alurrinum 580 370 $B 33000 a
Antimony U U Se --
Arsenic U U 7.5 or SB 3- 121
Barium 82 26 300 or S8 15-600
BeryMum U U 0.16 or S8 0- 1.75
Cadmium 0.6 U 10 or SB 0.1 - 1,(10"')
Calclum 1400 1600 S8 130-35000
Chromium 3 3 50 or SB 1.5-40-,(50...
Cobalt U U 30 or SB 2.5-60
Copper 12 8 25 or 88 1 -50
Iron 750 400 2000 or SS 2000-550000
Lead 35 44 SB 200-500"
Magnesium 220 400 SB 100-5000
Manganese 5s 26 SB 50-5000
Mercury U U 0.1 0.001 -0.2
Nickel 6 U 13 or SB 0.5-25
Potassium U U SB 8500-43000
Selenium U U 2 or 88 0.1 -3.9
Siver U U so -- o
Sodium 600 310 SB 6000-8000
Thaftm U U as --
Vanadium 150 or 88 1 -300
W
Zinc 20 or SB 9-50
A
Qualil lers: Notes. N
U:Compound analyzed for but not detected. --- : Not established.
NT:Not tested for. :New York State Background.
SS.Site Background. :Background for metropolitan or suburban areas.
Proposed revised criteria for ca"urn and
chromium In TAGM 4046 Appendix A.
El:Exceeds Recommended Soil Cleanup Objective.
T
b
Rl
SOUTHMEr.W-WOW 0x26199
W
f0
MAY-27-99 15 :40 FROM: ID: 516345 PACE 4/9
TABLE 2
SOUTHOLD LANDFILL
GLASS SAND SAMPLING RESULTS
VOLATILE ORGANIC COMPOUNDS
SAMPLE IDENTIFICATION NP-COMP NYSDEC
DATE OF COLLECTION 05/14/99 TAGM 4046
DILUTION FACTOR 5 APPENDIX A
PERCENT SOLIDS 94% CRITERIA
UNITS (Ug/k /k
Dichlorodifluoromethane U ----
Chloromethane U ----
Vinyl Chloride U 200
Bromomethane U
Chloroethane U 1900
Trichlorofluoromethane U --
1,1-Dichloroethene U 400
Carbon Disulfide U 2700
lodomethane U —
Acetone 180 200
Methylene Chloride U 100
trans-1,2-Dichioroethene U 300
1,1-Dichloroethane U 200
Vinyl Acetate U
2,2-Dichioropropane U
cis-1,2-Dichloroethene U --
Methyl Ethyl Ketone 260 —
Bromochloromethane U —
Chloroform U 300
1,1,1-Trichloroethane U 800
Carbon Tetrachloride U 600
1,1-Dichloropropene U —
Benzene U 60
1,2-Dichloroethane U 100
Trichloroethene U 700
1,2-Dichioropropane U —
Dibromomethane U ---
Bromodichloromethane U —
2-Chloroethyl Vinyl Ether U ---
cis-1,3-Dichloropropene U —
4-Methyl-2-perdanone U 1000
Toluene U 1500
trans-1,3-Dichloropropene U —
1,1,2-Trichloroethane U --
Tetrachloroethene U 1400
1,3-Dichioro roane U 1 300
$0VTKV0LWK4/mr 1 of 2 0&2"
MAY-27-99 15:41 FROM: • ID: 516345 PACE 5/9
TABLE 2(continued)
SOUTHOLD LANDFILL
GLASS SAND SAMPLING RESULTS
VOLATILE ORGANIC COMPOUNDS
SAMPLE IDENTIFICATION NP-COMP NYSDEC
DATE OF COLLECTION 05/14/99 TAGM 4046
DILUTION FACTOR 5 APPENDIX A
PERCENT SOLIDS 94% CRITERIA
UNITS u lk u
2-Hexanone U -—
Dibromochloromethane U --
1,2-Dibromoethane U ----
Chlorobenzene U 1700
1,1,1,2-Tetrachloroethane U --
Ethyibenzene U 5500
Xylene (total) U 1200
Styrene U —
Bromoform U ---
lsopropylbenzene U ----
Bromobenzene U ----
1,1,2,2-Tetrachloroethane U 600
1,2,3-Tdchloropropane U 400
n-Propylbenzene U —
2-Chlorotoluene U ---
4-Chlorotoluene U ----
1,3,5-Trimethylbenzene U —
tert-Butylbenzene U ----
1,2,4-Tdmethylbenzene U ----
sec-Butylbenzene U ---
1,3-Dichlorobenzene U 1600
4-Isopropyltoluene U —
1,4-Dichlorobenzene 110 8500
1,2-Dichlorobenzene U 7900
n-Butylbenzene U —
1.2-Dibromo-3-chloropropane U —
1,2,4 Trichlorobenzene U 3400
Hexachiorobutadiene U ----
1,2,3-Tdchlorobenzene U —
MTBE U —
Naphthaiene 59 13000
TOTAL VOCs 609 10000
Qualifiers:
U: Compound analyzed for but not detected-
Notes-
Not
etected_Notes-Not established
SOU WOL.WKahra 2 of 2 05(2m
MAY-27-99 15:41 FROM: ID: 516�04S PAGE 6/9
TABLE 3
SOUTHOLD LANDFILL
GLASS SAND SAMPLING RESULTS
SEMNOLATILE ORGANIC COMPOUNDS
SAMPLE IDENTIFICATION NP-CO NYSDEC
DATe OF COLLECTION 05114]W— TAGM 4046
DILUTION-FACTOR1 APPENDIX A
PERC NTS L CRITERIA
UNI (uglkg) (u g)
Phenol 500 J 30 or MDL
bis(2-Chioroethyi)ether
2-Chlorophenol U 800
1,3-Dichlorobenzene U 1600
1,4-Dichlorobenzene 740 J 8500
1,2-Dichlorobenzene U 7900
2-Methylphenol U 100 or MDL
2,2'-oxybis(1-Chloropropane) U ----
4-Methylphenol U 900
N-Nitroso-di-n-propylamine U ----
Hexachioroethane U ---
Nitrobenzene U 200 or MDL
Isophorone 370 J 4400
2-Nitrophenol U 330 or MDL
2,4-Dimethylphenol U
bis(2-Chloroethoxy)methane U --
2,4-Dichlorophenol U 400
1,2,4-Tdchlorobenzene U 3400
Naphthalene U 13000
4-Chloroaniline U 220 or MDL
Hexachlorobutadlene U --
4-Chloro-3-methyiphenol U 240 or MOL
2-Methylnaphthalene U 36400
Hexachlorocyclopentadiene U ---
2,4,6-Trichlorophenol U ---
2,4,5-Trichlorophenol U 100
2-Chloronaphthalene U ----
2-Nitroanillne U 430 or MDL
Dimethylphthalate U 2000
Acenaphthylene U 41000
2,6-Dinitrotoluene U 1000
3-Nitroaniline U 500 or MDL
Acenaphthene U 50000
2,4-Dinitrophenol U 200 or MDL
4-Nitrophenol U 100 or MDL
SOUTSEMINK41mr Paye 1 of 2 O"26M
I D= 51636045 PAGE 7/9
MAY-27-99 15 42 FROM:
TABLE 3 (continued)
SOUTHOLD LANDFILL
GLASS SAND SAMPLING RESULTS
SEMIVOLATILE ORGANIC COMPOUNDS
SA PL ID NTIFIGATION NP-COMP NYSDEC
D TE OFC LLE 05/14/99 TAGM 4046
DL� I AC OR 1 APPENDIX A
CENT OLID 94/o CRITERIA
U I S (ugh (
U8200)
Dibenzofuran U _.
2,4-Dinitrotoluene U 7100
Diethylphthalate U
Fluorene U
4-Chlorophenyl-phenylether U r�
4-Nitroaniline U
4,6-Dinitro-2-methylphenol U
N-Nitrosodiphenylamine U
4-Bromophenyl-phenylether U 410
Hexachlorobenzene U 1000 or MDL
Pentachlorophenol U 50000
Phenanthrene U 50000
Anthracene 960 J 8100
Di-n-butylphthalate U
Carbazole U 50000
Fluoranthene U 50000
Pyrene 10000 50000
Butylbenzylphthalate U ----
3,V-Dichlorobenzidine U 224 or MDL
Benzo(a)anthracene U 400
Chrysene U
313'-Dichlorobenzidine 6300 50009
bis(2-Ethylhexyl)phthaiate 50000
Di-n-octylphthalate U
U 1100
Senzo(b)fluoranthene U 1100
Benzo(k)fluoranthene U 61 or MDL
Benzo(a)pyrene U 3200
indeno(1,2,3-cd)pyrene u14 or MDL
Dibenzo(a,h)anthracene U 50000
Benzo(g,h,i)perylene
Qualifiers:
U: Compound analyzed for but not detected.
J: Result found below CRDL, value estimated.
Notes: Value exceeds the
Not established. NYSDEC TAGM Criteria.
MDL: Method Detection Limit.
o
page 2 of 2
S0U7SEMI.WK41mr
TABLE 4
SOUTHOLD LANDFILL K
GLASS SAND SAMPLING RESULTS N
PCBs
. m
SAMPLE IDENTIFICATION NP-COMP NYSDEC
DATE OF COLLECTION 05/14/99 TAGM 4046
DILUTION 1 APPENDIX A
PERCENT SOLIDS 94% CRITERIA a°
UNITS (U91k9) (ug/kg
Aroclor-1016 U ----
Aroclor-1221 U ----
Aroclor-1232 U ----
Arodor--1242 U ----
Aroclor-1248 U ----
Aroclor-1254 U ----
Aroclor-1260 U ---
TOTAL PCSs 0 J. 10000"
Qualifiers:
U: Compound analyzed for but not detected.
Notes:
----: Not established.
NA: Information not available.
Criteria is for total PCBs in subsurface som.
A
N
'fl
b
C'1
M
S0VPCPE8.WK4Jrnr asam
m
to
MAY-27-99 15 :43 FROM: ID: 5163145 PACE 9/9
TABLE 5
SOUTHOLD LANDFILL
GLASS SAND SAMPLING RESULTS
PESTICIDES AND HERBICIDES
SAMPLE IDENTIFICATION NP-COMP NYSDEC
DATE OF COLLECTION 05/14/99 TAGM 4046
DILUTION FACTOR 1 APPENDIX A
PERCENT SOLIDS 94% CRITERIA
UNITS k u
Pesticides
Endrin Ketone U
alpha-BHC U 110
gamma-BHC (Lindane) U 60
Heptachlor U 100
Aldrin U 41
beta-BHC 5.6 P 200
delta-BHC U 300
Heptachlor Epoxide U 20
Endosulfan I U 900
4,4'-DDE U 2100
Dieldrin U 44
Endrin U 100
4,4'-DDD U 2900
Endosulfan II U 900
4,4'-DDT U 2100
Endrin Aldehyde U —
Methoxychlor U
Endosulfan Sulfate 2.8 1000
Toxaphene U
alpha-Chlordane 2.5 540
gamma-Chlordane 4.1 540
Herbici e�
2,4-D U 500
2,4,5-TP Silvex U 700
Qualifiers:
U: Compound analyzed for but not detected.
P: Concentration estimated, possibly biased low since
primary and confirmation column concentrations had a
%D >25%, lower value reported.
Notes:
Not established
S0UPCPES.WK41mr 05/26/99
s
WASTE MANAGEMENT
123 Varick Avenue
Brooklyn,NY 11237
(718)533-5308
(718)533-5170 Fax
August 25, 1999
Mr. James Bunchuck
Solid Waste Coordinator
Town of Southold
Solid Waste District
P.O. Box 962
Cutchogue,NY 11935
Re: Southold Landfill — Acceptance of Glass Sand from Waste Management's 485
Scott Avenue, Brooklyn,NY facility
Dear Mr. Bunc tx
WM received your letter dated August 18, 1999 regarding the Acceptance of Glass Sand at
the Town of Southold Landfill and the proposed protocol for stockpiling and sampling the
material prior to using it at the landfill. WM has reviewed the protocol and accepts the
protocol as described in the letter. The following additions should be made:
1. The Town of Southold will send the samples for analysis to Waste Management's
contracted laboratory via Federal Express or other overnight mail service:
Willie Urbiztondo
Vice President, Sales
Accredited Laboratories, Inc.
20 Pershing Avenue
Carteret,NJ 07008
(732) 541-2025
2. The results of the sample analysis will be seat by Accredited Laboratories to Stan.
Fernandez of Waste Management. Stan Fernandez will review the results and share
the results with the Town of Southold (Jim Bunchuck) and the New York State
Department of Environmental Conservation (Ernie Lampros).
3. Waste Management will pay for the sample analysis.
Waste Management looks forward to delivering glass sand to the Town of Southold.
Please call me with any additional questions at (718) 533-5308 and to schedule the
commencement of deliveries.
Page 2-Letter to James ithuck
' August 25, 1999
Very Truly Yours,
Waste anagement of New York, LLC
araJ. e mer
Divisi ngineer
cc: Bob Boorum, Waste Management
Stan Fernandez, Waste Management
Charles Gusmano, Waste Management
0
�S FFO(
�0 G
JAMES BUNCHUCK P.O. Box 962
CZ
SOLID WASTE COORDINATOR Cutchogue, New York 11935
p Tel: (516) 734-7685
41 �aOl� Fax: (516) 734-7976
SOUTHOLD TOWN
August 18, 1999 SOLID WASTE. DISTRICT
Tara Hemmer
Waste Management of New York
123 Varick St.
Brooklyn, NY 11222
Re: Southold Landfill
Acceptance of Glass Sand
Dear Ms. Hemmer:
Following up on our recent discussions, presented below is a proposed protocol for stockpiling
and sampling the glass sand prior to using it at the landfill. The protocol is intended to meet the
Department's requirements for monitoring the chemical characteristics of the glass sand received
at the landfill.
1. Glass sand delivered to the landfill will be placed in a dedicated stockpile.
2. When approximately 5,000 cubic yards have been stockpiled, a representative sample
of the stockpile will be collected and sampled.
3. Four (4) grab samples will be collected from the stockpile. One (1) grab sample will
be collected from each side (north, east, south and west) of the stockpile. The grab
samples will be collected at a depth of approximately 3 feet from the surface of the
pile. A shovel will be used to dig approximately 2.5 feet into the pile at each grab
sample location. A disposable plastic scoop will be used to dig the last 0.5 feet into
the pile and collect the samples.
4. The grab samples will be composited into a single representative sample at the
analytical laboratory. A portion of one grab sample will be analyzed for target
compound list(TCL)volatile organic compounds(VOCs). The composite sample will
be analyzed for TCL semivolatile organic compounds, pesticides and PCBs and target
analyte list (TAL) metals and cyanide. The laboratory used will be a laboratory that
has been certified by the NYSDOH under the environmental laboratory approval
program (ELAP). A laboratory turn-around time of one-week will be requested and
the results will be forwarded to the NYSDEC upon receipt.
Tara Hemmer
Glass Sand Sampling Protocol
August 18, 1999
p. 2
5. Beginning on the date that the stockpile is sampled no additional material will be
added to the stockpile. Incoming deliveries of glass sand will be placed in a new
stockpile.
6. Upon receipt of approval from NYSDEC, the stockpile which has been sampled and
tested will be used for backfilling the former lagoons and/or general contour grading.
7. The procedure described above will be repeated for each 5,000 cubic yards.
8. If at any time the NYSDEC finds the results of the analyses to be unacceptable, Waste
Management will remove the stockpiled glass sand from the landfill. Within 5 business
days of notification from NYSDEC, Waste Management will submit a letter to
NYSDEC, with a copy to the Town, identifying the proposed procedures to be used
for removal of the glass sand from the landfill and transport and disposal. Waste
Management shall remove the stockpiled glass sand from the landfill within
10 business days of the date of approval from NYSDEC. All work required to remove
rejected glass sand from the landfill shall be the responsibility of Waste Management.
Please contact me as soon as you have reviewed and approved the above or if you have any
questions, so that we may begin to accept the glass sand at the landfill again and continue our
contour grading work in support of closure efforts.
Very truly yours,
ames Bunchuck
Solid Waste Coordinator
cc: Supervisor Cochran
Greg Yakaboski
Ernie Lampro,NYSDEC
Bob Boorum, Waste Mgmt.
T. Maher, D&B
D. Glass, D&B
05%19%941 08:57 FAX 183152 WASTE MCMT 0 C7 o
%*Ira
WASTE MANAGEMENTC
c -
101 Varick Avenue, Brooklyn, NY 11237
718. 61~'3 51 v(0
FA" COVER SHEET
THIS INFORMATION CONTAINED IN THIS FAXS{MILE AND THE DOCUMENTS ACCOMPANYING THE FACSIMILE
CONTAIN INFORMATION FROM WASTE MANAGEMENT WHICH IS CONFIDC•NTIAL ANLVOR LEOALLY PRIVILEGED.
THE INFORMATION IS INTENDED ONLY FOR THE USE OF THE INDIVIDUAL OR ENTITY NAMED IN THE
TRANSMITTAL SHM,IF YOU ARE NOT THE INTENDED RECIPIENT.OR THE EMPLOYEE OR AGENT RESPONSIBLE
TO DELIVER IT TO THE INTENDED RECIPIENT. YOU ARE HEREBY NOTIFIFI)TIIAT ANY DISCLOSURE,COPYING,
DISTRIBUTION. DISSEMINATION OR THE TAKING OF ANY ACTION IN KL.'LIANC'L• UPON THE CONTENTS OF THIS
FACSIMILE ARE STRICTLY PROHIBITED: AND THE DOCUMENT SHOULD BE RETURNED TO OUR FIRM
IMMEDIATELY. IF YOU HAVE RECEIVED THIS FACIMILE IN ERROK, PLEASE NOTIFY US BY TELEPHONING
IMMEDIATELY SO THAT WE CAN ARRANGE FOR THE RETURN OF THE ORIGINAL DOCUMENTS AT NO COST TO
YOU.
DATE: �� • ��
TO: S1 PA2VN CC COMPANY: S0VS N0L-Q 1•ftWO
TITLE:
TELEPHONE: FAX#: (S I�o ���'�
FROM: Smkw Feet-/*wims
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05/19/99 08:57 FAX ftl83152 WASTE MGMT Oft Zo3
05/19/08 15:25 FAX 1 732WI 1333 ACCREDITED L.ASORATOW" 004
ACCREDITED LABORATORIES, INC .
TCLP VOLATILES ANALYSIS DATA
CASE HUMBER 4261 MRTkIX Lsach�4� �i
SAMPLE NUMBER i, 99IQ4772 DILUTION FACTOR 10
DATA FILE :42491 OATE EXTRACTED
CLIENT NAME ,. 1KLuI i DATE ANALYZED 4 14 99
FIELD ID CGS ANALYZED BY
a0 erias��s�z�ao�cwws.P.s cR�sYa•sec.s=�=y11CQaf•MY�Wtri=xmx=�=ss.-�T.i»ii�Si��r��1�s19iCC73
RFyulatory
WILLIAM -
LAS No . Compound Insult 11DL Level
a�'xc�aeisa�S�If1�Ysooc�s�aysc�sascnxl�tms��c����1�A�lax�xs�x±===scs�slA��FiR�Ps aic
71432 Benzene U
78933 2-Butangne U . 100 200 , 0
56235 Carbon Tetrachloride U . 050 0 . 5
108907 chlorobenzene U . 050 100 . 0
61963 Chloroform U . 050 6 . 0
7!,354 1 , 1-Dichloroethene U . 050 0 . 7
107062 1 ,2-0tchlaromthane U 1050 0 . 5
17.7184 Tetrachloroathene U . 050 017
79016 Trichleroethene U
. 050 0 . 5
75014 Vinyl Chloride U 100 012
-5URR_OGATE. COMPOUNDS RECOVERY LIhLLT-s iJ5
1 ,2-Dichloroetfiane-d4 87 '` 76 - 114 OK
To l4ene-do 95 Y. 88 - 110 OR
Bromofluorebenzene AB Y, . 86 - 115 UK
(U) Indicates compound was analyzed for but riot detected ,
E Indicates result exceeds highest calibration standard .
D - indicates result is based on a dilution .
* 2-Butanone a MethV ! ethyl ketene
05/19/99 08:57 FAX 7 83152 WASTE MGMT 0
04/18/99 15:30 FAZ 1 73*1 183 ACCREDITED LA80RATOO S G1007��a
ACCREDITED LA60RATORIE$ y INC .
TCLP SEMIUOLATILES ANALYSIS DATA
CRSE NUMAFR 4281 MATRIX LeDohMjSZ
SAMPLE NUMSF:k, 2994ZZZ DILUTION FACTOR 10
ORTR FILE >F8306 DATE EXTRACTED 0°;/17/9
CLIENT NAME W.MQNYDATE ANALYZED 02/17499
FIELD ID CGS ANALY29D BY JANICE
=7a�Arraoaga,�;v=sMaaaOya¢a¢zasoeearaa et=�=eat=�=sssa=y=mss=aRa¢arar�rrrr-r-rr-�
Regulatory
Rp�c l t MOL Loue l
CAS No , Ca(Apdund
=��i4Y====r=ra-t==tiFiaarrrxrG!!-=QaaPQ3iririrYtl==��=Gv4=i.371aai.....aawawaw .a�
110A41 Pyridine U . 10 5 . 0
106467 1 ,4-Dichlarnbenzene U . 10 7 , 5
95478 2-Methylphenol U . 10 200 . 0
109394 3&4-Methylphenol U . 10 200. 0
67721 Hexarhloroethane U , 10 3 . 0
989103 Nitrobenzene LI . IO 2 . 0
87683 Hexachlarobutadiene U . 10 0 , 95
08062 2,4,6-Trichlorophenol 1,1 . 10 7 . 0
9109104 2 ,4.5-Trichloraphcnol U . 50 400 . 6
121142 2,4-pinitratoluene U . 10 0 . 13
118741 Hexachlarobenzene U . 10 0 . 11
878610 Pentaehlererhenol U . 10 10010
U 0 Pr1 S Rcr,•nvEgy LIMITS 5TIRTUA
Z-Flucrophenol vz 2 21 - 100 OK
Phenol-d5101 X 10 - 94 OUT
Nitrobenzene-dg 97 X 35 - 114 OK
2-Fiuorubiphenyl 84 % 43 - 116 OK
2,4,4-Tribroaeophenol 77 x 10 - 123 UK
Tvrphanyl-d14 77- Y� 33 - 141 OK
U tndicetas compound was analyrad for but not detected ,
E - Indicates result exceeds highest calibration %tandem; .
A -- Indicates rr_suit is based an a dilutten .
+' 2-Methylphenol a e-eresal
3-tlethyiphenol a m-cre501
« 4-Mithylphenal - p,-cresol
«* 3-•Methy 1 phena i and +4-Mathy l phena 1 can not be separated by the
method applied ,
05!19/99 08:57 FAX183152 WASTE MC,MT 0 Z05
03/18/09 15:30 FAC 1 T3 1 1383 ACCREDITED LABORATO 9 Q008
ACCREDITED L"ORATORIES, INC.
TCLP PESTICTD99 ANALYSIS DATA
CASE NUMBER _42_41 MATRIX
SAWLL NUMBER 99Q&232 DILUTION FACTOR
DATA FILE > DATE EXTRACTED
CLIENT NAME WHONY - -- DATE ANALYZED
FIELD Xb Cos ANALYZrD BY F
Regulatory
Result MDL Level
CAB No. Compound
58-69-9 G-9$C (Lindana) U .001 0.400
76-44-8 Haptachlor U .001 0. 008
1024-57-3 Heptachlor Epoxide U . 001 0. 008
72-20-8 Endrin U . 002 0. 02
72-43-5 Mathoxyehlor U .010 10.0
5103-71-9 A-Chlordane U . 001 0.03
5103-74-2 G-Chlordane U . 001 0.03
8001-35-2 ToYaphans V .050 0. 5
ADVISORY
SURROGATE--CG"OIJNDS
C LIMITS
- STATUQ
retrachlcro-m-xylene 13 It 30 - 150 o1C
U - Indicates compound was analyzed for but not detected.
E - Indicates result exceeds highest calibration standard.
D - Indicates result is based on a dilution.
05,119/99 08:57 FAX4183152 WASTE MGMIT [a 06
03/14/99 15:30 FAX 1 7 541 1383 ACCREDIM LABORAT ., Gh 009
ACCREDITED LABORATORIES, INC
TCLP HERBICIDE ANALYSIS DATA
CASE NUMBER MhTRIX ac
SAMPLE R MNER DILUTION FACTOR
DATA FILE � -60 DATE EXTRACTED
CLIENT NAME DATE ANALYZEDFZSLD ID ANALYZED BY
CLIFP
Result MDL
RBq�vei latory
CAS No. compound (mq/1)
94757 2,41-D U .100 10.0
93721 5ILVEX U .010 1.0
V - Indicates compound was analyzed for but not datacted
05/19/99 08:57 FAX 783152 WASTE MGMT OF 1607
05/18/99 16:94 FAX 1 712 1 1983 ACCREDITED LUORATOR 5 Qb003
ACCelD11Eb LABoMTvRIE6, INC.
REGRATEO TCLP i4f7me
INORUNIC ANALY811 DATA 114e►
Cost 0: _ 4261 Matrixc _ Lgggostu
Samp(t 9; 9994772Date Received: 05f III"
Field 1Os Cos
Clime New, WNTY
Result MDL OilutIOM Re#ulatory Date
CA* No. Element NC/L MG/l. Factor i.swl Method Analyzed
srrsaRsrrrssr_aa+�essM7taas�eeea�y:wav�a�c�•ar�w�w����M�s�e.�+e
7440.36-2 Atomic NO 1.00 1 S.00 P Oa/171"
7a10-39-1 8orhm .370 .100 1 100.00 ► 05/17/99
7440.63.9 Cww um ND .100 1 1.00 ► 05/17!99
7440.47.3 Chromium NO 1100 1 5.00 P 45118/1~
7430-92-1 Lead ND 1.00 1 5.00 / 09/12/99
7419-97-6 Mercury No .002 2 .20 CV 05/14/99
778,2-av-2 Beleniva ND .500 1 1.00 M 05/18/99
741[0.22-6 Silver NO .100 1 5.00 P 03/17/99
NO - EleeNnt wlyzod far but net dateet4a,
P - Analyzed by ICP Gy - Ansly&$d by Cold vapor
F - Analyzed by GFA A Anolyzed by flame AA
05,"191199 08:57 FAX4183152 WASTE MGMT Z08
03/18/99 13:28 FAX 1 73, 41 lady ACCREDITED L.A80RATOiriES 0 003
PCCAEDITEO LABOAATORIES, 1%.
VOLATILE ORGANIC ANALYSIS COTO
CASE NUMBER MATRIX Soil
SIMPLE NUMBER990411 _ _ DILUTION FACTOR i.o �`—
DATA FILE »1STQ" DATE EXTRACTED
CLIENT NAME YliO)1Y •
GATE R"LYZED 05117lQQ _
HELP 10 ,. CGS ANALYZED BY
r..as.swss■sacs_aeeeess:ssnsgaaxa�aa■s■:■_■ss:es.=.:.=svxsss •xx:eetssss===�s-;�rssssssasassssaaenee:ane=-es:.es.=.a.xss:
CA5 t COMPOUND USAG MOL tAS t COMPOUND U6/K6 MDL
efsesssrees.5555Rorole5855::sa■es■ee■■■eeesasaessss■:e::a■s■■ate... ss■■■■.■ssaaxs■esn■s.=:ss.===:sssv
ss■saavcs asas■aa urs.u•sa
!07029 ln U 26 75274 Bromodichloroeethane U 5
10701 .Acrylonitrile U 16 76875 1,Z-diohloropropane U 5
74973 Chloromethane U 5 10061015 cis-1,3-DichlvrvPrvpene V 3
74837 81'"owthens U 5 79016 Trichloroethene U g
73014 Vinyl Chloride U 5 71432 Benzene U S
15003 . Chloroethane U 3 124401 Dibroevchloromethene U 3
75092 Methylene Chloride it Js 3 74005 1,I,Z-Trichloroethane U 5
11694 Trichlorofluormthone 9 5 10061016 trans-1,341chloropr9pene U 5
75354 1,1-04hlorvethene U S 110756 2-Chloreethylvinylether U 5
75343 . 1,1-81chloroethant U 3 7525Z Brnofora 8 3
156605 trans-l,T-Oichlorasthene U 3 127164 Titrechlvroethene U 5
67663 Chloroform U 1 14 U5 1,1,2,2-Tetrochloroethane U 1
107012 1,Z-Olebloroethane U 5 108003 Toluene 5 J 5
71556 1,1,1-Trichloroethane U 5 108907 Chlcrobenrene U 5
562!1 Carbon Tetrachloride U 3 100414 Ethylbenzene U 5
7P F '@,L... .. Mi i U
1,2-0 iehloroethane-d4 �� >: 10-121 B—
tv l uene-d8 �1Q1 t 01-117 alt -
Sromoflvorobenzene 7A >i 74-171
Percent solid of 97.1 Is used for all target compounds,
3 - IndicateS compound concontratlon found balou MOL, B - Indicates ocepound found in associated block.
U - Indicates compound analyzed for but not dtteoted, F • Indicates fesult exceeds highest calibration standard
0 - Indicates result is based oA a dilution. A - Result exceeds residential svrface soil standards.#
1 - Result exceeds Industria] surface soil standards,o
+ Flags are based on Ner Jersey soil Cleanup Criteria from Site Rawdiation News Volume 06 Number 1.
05/19/99 08:57 FAX4183152 WASTE MGMT Y Ca 09
09/18/99 15:29 FAX 1 73Z'�541 1383 ACCREDITED LABORAT ES 0 005
ACCREDITED LABORATORIES, INC,
BNA ORCANIC ANALYSIS DATA
CASE NUMBER 4181 i1ATRIK Sail
SAMPLE NUMBER 9904171 DILUTION FACTOR 1.0
DATA FILE >F8179 DATE EXTRACTED OS/12/99
CLIENT NAME W1DNY DATE ANALIZED 05/19/99
FIE11) ID CCS ANALYZED BV DANIEL
==s===35:513 railw.:..seymawsate=i!lae=sw=e:caataeesillaaa.wm wflwmfmmwffff iffaaamisa=waw wawwsia;off aaaf aaffaaafrrmaamfff.
CAS Ii COMPOUND U5/K5 MDL CRs 11 COMPOUND UC/KC MDL
eab rr..arwr�rlsi„elsssesa=www�lawf¢sf aaaaiaq a:mcom s�w►sv :eeeeeef=e==e=ams==�z;a,atssssalusselsffwaaifff sfsRss.as:w
03329 Ace"aphthene U 540 51265 2,4-Dinitrophemol U 340
208468 Acenaphthylene U 340 111147 I,4-910 trotoluene U 340
120127 Anthracene 0 340 606202 2,6-Dinitrotoluene U 340
56559 Benzo(a)Rnthraosne U 340 117840 01-n-00tyl phthalate 3404 340
30328 6s926(a)Pyrehe U 340 246440 Fluaranthene 99 j 340
201912 Benzo(b)fluoranthene U 340 86737 Moreno D 140
191242 Benzo(g,h,i)PeryleRe U 340 118741 Nexaehlerebentene U 3`0
207089 Benzo(k)Fluoraothene U 340 87483 Nexschiorabutadiene U 340
65050 kbhtgic Acid 290 J 1700 77474 Kexachl4rocyclapents4iene U 340
100516 Renzyl Alcohol U 340 67721 Nexachlo►oethaee U 340
111444 bis(-2-Ch1oroethy1)Ether U 340 IF5395 Indeno(1,1,3-cd}Pyrene U 340
100601 bls(?-Chloroisopropyt)ether U 340 70591 Isophorone U 344
117811 8is(I-Ethylheryl)Phthalate 3890 340 91576 2-1%thyln4phthslene 77 J 140
111911 bisl•2-Chlornethozy)tivthane U 340 93481 7-Mtthylphenol U 340
101553 4-6rovaphenyl-phsnylether U 340 108394 364-Methylphendl 52 J 340
05687 Butylbentylphthelote 7300 f 940 91203 Naphtholene 1300 940
106478 4-Chloreanilipe U 340 88744 I-Nitroanlline U 340
91587 2-Chloronaphthelene U 340 99092 3-4itrasO line U 340
39507 4-Chlera-3-wthylphenol U 340 100016 4-Nitroaniline U 340
95370 2-Chlorophenol U 340 98933 Nitrabentena U 340
7005723 4-Chlorephenyl-phenylether U 340 08755 2-111trophenol U 340
218019 Chrysene U 340 100027 4-Nitrophen4l U 340
$3703 Dibenzo(a,h)Anthracene U 740 62790 N-Nitrosodimethylasine U 340
132649 Dikhx0foran U 340 86306 M-Nltrasodiphenyfamine U 340
95501 1,21ichlor0enzene U 340 621647 N-Nitrosv-Di-n-propylaalne U 340
541731 1,3-8iehlorobenzene U 340 87865 Pentaehloropheh41 U 340
106467 1,4-Dichlorobentene 170 J 340 05018 Pheneathrene 150 3 340
91941 3,31-Dichiorobentidine U 340 106P52 phenol U 340
110932 2,411chloropheno) U 340 W000 Pyrene 210 J 340
84662 Diethylphthalate 640 340 110821 1,2,4-Trichlorobenxehe U 340
105679 2,4-Dimethylphenol 0 340 95954 44.5-Trichlorophenol U 340
131113 Dimethyl Phth4lete 120 a 340 88062 2,4,6-Trichlorephenal U 340
84741 Di-n-Butylphthoiote 2100 340 928f5 9en:idine U 340
534511 4,6-Dinitro-2-sethylphenol U 340 123667 1,2-Dipheny1hydratine U 340
jURROCAT1 C81FAM OS 1601ily. _ S7 Til
Nitrobenzene-d5 ---y X 13-120 -OK
2-Fluarobipheh9l --X 2 50-i15 0K_
Terpheny1-4114 ..+.1: 4 18-137 Ok
Phenol-415 �_Be t 74-113 ,,.9-
141uoropheno1 79 x 75-121 U
2,4,6-Tribroaophenol 11 li 19.121 —OK_
Percent solid of 97.5 is used for all target compounds,
J - Indicates compound concentration found beloo MOL, e - Indicates coapaund found in associated blank.
U - Indicates compound analyzed far but not detected, E - Concentration sroeeds highest calibration standard,
0 - Indicates result Is based on 4 dilution.
of 3-liethylphenol and 4-Methylphenol can not be separated by the method applied
05%19;99 08:57 FAX83152 WASTE MGMT (a 10
05/18/00 13:29 FAX 1 732#41 1983 ACCREDITED LABO ATC 9 2006
ACCREDITED LABORATORIES, 1W
INA ORGANIC ANALYSIS DATA
CASE 1411MBER 4 MATRIX Sail
SAMPLE NUMAF.R 994477201 DILUTION FACTOR 5
DATA FILE HIM DATE EXTRACTED 054121?1
CLIENT NAME _ 04147. . _ DATE ANALYZED 21/1Usy
FIELD 10 CGS "10710BT DANIEL �
•iiiYYYiiiiYYvasvvss l�filiiiszzsrsrrzssaave�e7'zr=ravna=i_ea yrea:rY!ree=lilSCY iIiYiYYvv4v444a�iYiYfi7aia001Yf a...........
EAS 0 EOnP0UN0 U9/9G ADL Cos 6 COMPOUND OF/H DOL
:■eiiYiliiblrl=a2i$C�::YiYYYYYYYYY!l���\i������iiYvvvlv4xtYv ---==a==4rr4r4viYYYiai/iY�YYY■YYYYl�iYY!!!l7Yf Y!!b_a=asrrrea
1331! Acenaphthene U 1700 51285 214-Dinitrop4nal U 1700
200968 Acenaphthylene U 1700 121142 2,441 0trotoluene U 1700
120127 Anthrecene 11 1700 606702 2,6-0initrotolaane U 1700
56553 Benvo(a)Anthracene U 1700 117640 01-n-octyl phtheiate 7800 0 1700
50370 90":o(e)Pyrene U 1700 ?06440 F)uarantWne U 1700
?05911 Bento(b)fluoranthene U 1700 06737 Fluorene U 1100
191142 Be112e(9,111i)Perylene U 1700 110741 HeKachlerebeezene U 1700
207089 Benao(k)Fluoranthene U 1700 67683 lkxechiorobvtadlene U 1700
43850 BeOtole Acid U 8500 77474 Nrlrichlorocyclopentadiene U 1700
100516 Benzyl Alcohol U 1700 67721 Nexaehloroethane U 1700
111414 bis(-I-Chloroethy))Ether U 1700 193395 1ndeno(1,2,3-cd)Pyrene U 1700
108601 bis(Z-Chloroisopropyl)ethar U 1700 70591 isophorone U 1700
117817 Bis(2•Ethylhexyl)Phthalate 3800 0 1700 91576 2-Methylnaphthalene U 1700
111911 bis(-Z-Chloroetho�y)Methane U 1700 95497 2-Methylphenol U 1100
101453 4-Broaophenyl-phenyltther U 1700 100394 394-Methylp4nol U ' 1700
03617 Autylbentylphthelate 6100 O 1700 91203 Naphthalene 1500 3 0 1700
106471 4-Ehloroaniline U 1700 88744 7-111troanlllne U 1700
91587 2-Chiaronaphthalene U 1700 99007 ;-Nitroeniline U 1700
"IQ? 4-Chloro-3-vothylphenol U 1700 100016 4-4i1roanlline U 1700
95570 2-Chlorophenol U 1700 98953 Nitroteniene U 1700
7005773 4-Chlorophenyl-pheny)ether u 1700 88755 1-Nitrophenol U 1700
218019 Chrysene U 1700 100027 4-111t►ophenal 0 1100
53707 01ben:o(a,h)Anthracene U 1700 62759 N-NitrosadlaethylaMlne U 1700
112649 Oihenzofuran U 1700 96304 M-Nitrosadlphenyleslne U 1700
95501 1,1-Dichlorobenrene 0 1700 67.1647 N-Nitroso-Di-n-propylan�ine U 111,0
541731 1,3-Dlohloroben7ene U 1700 8186; Pentachlorophenol b 1700
106467 1,4-Dichlorobenzene 170 J 0 1700 65018 Phenanthrene 170 3 O 1700
P1941 5,3'-Oichlorobenzidine U 1700 108952 Phlnpl U 1700
170132 2,4-01chlorophenal U 1700 WOOD Pyr"n U 1700
84667 Diethylphthalste iD00 J 0 1700 120621 1.2,4-Trithlorobenxene U 1700
105679 Z,4-Oiwthyiphenol U 1700 951% 2,4,5-Trichlorop1wenol U 1700
17111) Oi"thyl phthalate U 1700 88067 7,4,6-Trichlorophenol U 1700
0474? 01-0-Outylphthslate 2600 D 1700 92975 Benzidine U 1700
574521 44-0 44pa-7-eethylphenol U 1700 122467 1,2-Dipheny1hydru the U 1700
SURRQGAJE Email ACV R 1-I111ts ST�ATU5�
Mitrabenzene-d6 —,Sj 1; 23-120 OK_
t-Fluarobiphenyl .—w x 30-115 -JL-
Terphenyl-dl4 j t 18-137 , OK
phenol-d5 _j� t 24-113 OUT
2-Fluerephenol � 2; 25.171 OA
2,4,4-Tribre"plimal _�3 x 11.121 DR",
Pereent solid of 973 Is used for all tatget coepeunds.
J - Indicates coepound concentration found below MDL, I - Indicates covq*und found in associated blank.
0 - Indicates compound analyzed for but not detected. E - Concentration exceeds highest calibration standard,
0 - Indicates result is based an a dilution,
rr 3-ilethylphenol and 4-Methylphenol pan not be stpareted by the Method applied
` 05/19/99 08:57 FA84183152 WASTE MGMT Y fall
09/16/60 1'3:30 FAX 1 7 541 1383 ACCREDITED LABORA IES Gh 010
' ACtlt®ITER LABORATC�IES, ItMC
PISTICIOUPC9 ORGANIC ANALYSIS DATA
GSE Mtimal -4jM1 MATR I It Eoi
!AMPLE NUMBER _ DILUTION FACTOR
DATA FILE >Ai636 DATE MRACTEO
CLIENT NAME DATE AMALYZM T g5ju 9
ftELD ID �CQI ANAITM BY Guff
�=ss�aaaaaaasa�.wsaaasa
CAS4 COMPOUND Uq/RG IOL
319346 A-SNC
311067 B-iNC 24.0 .664
"M 6-BMC tL hMuna1 u .664
319666 D-Mc u ,d"
76403 Boptsobter 6.69 .664
309002 Aldrin u -654
1024573 Meptschlor 1poxide 04.7 .66t
999944 EnQoautfen 1 17.9 .684
0103719 A-chtord" u -6"
$103742 G-chlordane 1618 .684
60971 01stdrin 2.06 1.37
72559 4,40-00E 10.9 1.37
72204 morin u 1.37
Ml$#39 /ndeeulfen 11 u 1.37
72548 4,48-000 2.0 1.37
7421934 EnCIrin Atdohyde u 1,x7
1031078 Endosulfan Sulfate u 1.37
so 4,41.ODT 192 1.37
SM94705 Erdrrn Ketone u 1.37
72435 Methoxychlor u 6.84
M01362 TaxeMwm u 34.2
1267411= Aracior-1016 u 17.1
11104282 Armtor•1221 u 1711
11141163 Aroclor-1232 u 17.1
53469219 APaetor•1242 u 17.1
12672196 APector-1243 u 17.1
11097601 Arocter-1854 u 17.1
110"09 Aroeler-1Zb0 u 17.1
Percent Solid of 97.1 14 uead for alt corset CONPou<uM.
e - yn
Irdicstes COMPO hd fod in assacisteq blank.
j - Indicates cosipMd concentration 43rd WON MDL.
u indieates eapau d anslysatl fen but not deteeted.
E - Indleatea resutt exeeede hisheat eatitwacion st&mmp d.
0 - indicates resutt is M06d an a dilution.
40
05/19/99 08:57 FAX 4183152 WASTE MGM Z12
05/18/99 16:33 FAX 1 13 41 1969 ACCREDITED I.ABORATO ES Qb002
ACCREDITED! LADORA7oRIES. INC.
INORGANIC ANALTSIS DATA SHEET
Case *; 4281 Matrix: - Mil _
Sample Ile 9906772 Date Receive43 06/12/99
Ffetd I0: M
Clfw7t Names ANNY
Result MDL altutlen Otte
CAS No. Etament MO/K8 MG es Factor Mlthnd Amtysed
=s�aa.T.sca��rsNeeA�leaee�canF��c��+ssw�ssaAlwwN��llC�as-�lt��
?"0.36-0 Antimww wa 4.4% 1 P 05/16/44
7440-39-2 Arsenic .7d8 .6w 2 F 09/17/09
7440-41-7' 6erYtttum No 1645 1 P 09/18/!1'
7440.43-9 Cedaium 1.20 .645 1 P 05/16/!!
7'440.47.3 Chromium 3.75 1.94 1 P 05/15/99
74+10-30-8 Copper 16.4 1,94 1 P 05/18/99
(439.92-1 - Leed 87.1 16.1 1 P 05/18/94
7439.97-6 Mereury .519 .205 1 e'V 05/14/99
7840-02-0 Nickel 11.9 2.54 1 P 05/18/99
7742-49-2 Selenium ND 1.31 2 F 05/17/99
7'440-22-4 Silver ND .645 1 P 05/18/99
7440-2e-0 Thattfum ND .662 2 F 09/17/94
7440-"-6 7fn0 1'J6 6.41 7 r 05/10/99
Percent Solid of 97.5 to used for ett terW ot~ts
NO - Etv"nt anelysad for but not detected.
0 -
Anely2ed by ICP CV - Analywad by Cold Vapor
F - AnalYcM bV GFA A - Anatyiad by flame AA
051,191,99 108:57 FA. 4183152 WASTE MGMT 'Y z 13
• 05/18/99 15:31 FAX 1 T3�S41 1383 ACCREDITED LABORA O IS moll
ACCREDITED LAYORATORIEC, INC.
SENI:NAL CRENISTRY ANALYSIS DATA
Cog* 0; 4p$1 KOCrlx. Ooil
Esxple 0: Date Received: 1
C1 font Nemec _ bMOMY _ X Moisture:
Ffe4d Nur"r: [{S
DILUTION METRA OLAMK ANALYSIS
ANALYTES RESULTS MDL UNITS FACTOR RrsuLry MDL DATE
Bolide, Perpent 9T.5 0.10 X 1, 03/131"
Flesh Point V200 80. •F 1. 03/13/99
PM 7.10 S.L1, 7. 0511Z/1!
cyanide, Reective No 0.21 RQ/Kr 1. NO 0.01 05/13/99
Sulfide, Reactive ND 41.0 No/Ke 1. NO 2.0 05/13/98
Totsf organic Carbon 9950. 106. /K8 1. ND 100. 09/14/"
HPR-13-1999 08:52 FRO7194362956 TO 15167347976 F.01
r
EnIviromhental Te'9fi ig Litbo"rat6t ies, Inc.
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2e iiv6d:;31,31199 40'00;:
Sampler!by`N/A
( POat it''Fkx Note 971, Date p
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Phone st.�--✓'G. 7 ,f'��4�'s" Phone N 7� 7.�5`p6 D0, ;
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&ia fronment�l.r oh L ratr�rie s,lrlb;
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NYS Lab ID # 10969
NJ Cert. # 73812
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VA Cert, # 108
CA Cert: # 2253
NH Cert. # 252592-BA
MA" Gert. #NY061 ,
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ACert. # 68-535
A�rhrhr� +�
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12148- Page 1
APR-13-1999 08:54 7184.362956 T 15167347976 P.02
Enviar�nnt nt�ti Test >t0 Labar tunes Inc.
zoo mute 109,farnlinodale i�! 11739 -Pl;irn��t:r-2a4�1�5G.Tax-S 1 G 2�9-8 44
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ANAILY3lS:ikeockt •TCLP -Metals
aggpi�12140.1
Cliont 3()mpla It): (;rushed Glass Collected: X130149
hAatrlY: Solid- Type:'Greb
RwiriarK�
Analyzed:412109 + Units pprri`
_ ...... MM�� - -�oiicari£rarlo� `�
1440,38-2 Arvdrn 0 Q�St� is 0 u,------- }
TAd0:33 3 j
arliI1 tlD 1
746� 3=9 Cddmr m t 4 �i t33i ;
'r fiI�37 3 �.Feromam �atl 1��$'� �7"
:7i - --4 -3- rpacJ Orb;.:
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7440w224 Silver
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APR-13-1999 08:56 FFO 7184.362956 TO 15167347976 F.03
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i Lnv'iroftibental Testing Laboratories, lac,
208 Rout' 109,nirmingdolr NY j1735 �hot+o 51G 249-1456 Nx•S1(,40-0144
4!5189
1A)RGA IC rviftlHOn QUAI:;ri URS
Q Uuelif ies-vPi•r led enities wtd thou meanings etc.0 folloWs;
t Tlic ai+alvii�;itl rYsult is a nhn:rlrtpct.
J lndreataa an et111111'a'W'Vdlti 'Mi!CM)":MiAtiot,Wgi dotocted,l�l ttr thin tht Contract
t?c�vired 17utdttleJ>LinLt,but�rr.$tn Ihan,the Tvlethild fietectran I„unit,
13. the w1ilyte,w65 found in the i1ocinicil rr>t:lhod blank ar 1ve11 as the s • I '
It Lnflicatt c pbuible%ptobablc bank coutalliirla6m mud wamc the All I=
taY9
�+1'T”^rrietr nrrfon
1 The,wrtcuiieitlon of tHP analyte ob�ceeil(mk the triolibration raise of
t11c jusiru1,1vn4
1) ''1`atts h ig idtttiifics a]I e0plowilli1,WrnrifIFM In an analytic 3t a•soc6hdary dilutiou.
Z.1TORI1—ANN ME7'1•!OD QUA:LME WS, q
C - (t'anee)itratlpn►gnniificro arc as tollowy,
I3 enicrr rf 1i rhp t+•pt,ited 1 aloe teas obtaiocci fYoru read;ig!hut k rc cess'
fltau the Cnmrarr RF.quL#6d Detection Lim t"(CRA )but�reaiet,t6ar,lir rtlnal
t�,tl+c Ifpio(rncnrPetecttnn 1.. t(101'),
t? ultttrcd 4cn'tht aimlyle w;r vnAlyzm 1�%r;hui'niai dcteated,.
Q - quafitiir, "pboifia cntritss ittid tbcar miAni.t+.es are Al fi,it+,rr s
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JAMES BUNCHUCK P.O. Box 962
SOLID WASTE COORDINATOR H Cutchogue, New York 1.1935
�y • T(+ (.1316) 734-7685
Fax: (516) 734-7976
SOUTHOLD TOWN
SOLID WASTE DISTRICT
August 27, 1999
MEMORANDUM
TO: Greg Yakaboski
FROM: m Bunchuck
SUBJECT: Glass Sand Letter Contract
Attached is a Draft Letter Contract/Agreement between Waste Management of New York
and the Town of Southold re: resumption of glass sand deliveries for the landfill capping.
I did not add any language re: the requirement of a surety or bond on the part of Waste
Management. I'm not really sure where to go with that . . Do we want 1)to ensure
simply that they would remove a pile that tests bad, or 2)would we be looking for them
to possibly remove all the glass sand delivered due to a potential future problem, even if
the DEC had approved its use?or 3)perhaps are you thinking of even broader future
damages or remediation costs should the landfill ever pose a threat down the road? If
either 2)or 3)I don't think we'd ever get Waste Management to agree. There are too
many things that have been dumped in the landfill over the years for them to take on that
liability.
If you want to pursue this, perhaps you could call Tara Hemmer of Waste Mgmt. and go
over it with her? Otherwise, if this agreement seems good to you, I'd like to bring it to
the Board. Let me know what you think . . .
JIM
0
* * *DRAFT PROPOSED CONTRACT
RE: "Waste Management's Glass Sand"
August 27, 1999
Tara Hemmer
Waste Management of New York
123 Varick Street
Brooklyn,NY 11222
Dear Ms. Hemmer:
I am writing in response to Waste Management's offer to deliver fill to the Town of Southold for
use as grading material at the Cutchogue Landfill.
As you discussed with Jim Bunchuck of my staff, your offer is to deliver the glass sand on an
ongoing basis at no cost to the Town. The Town is prepared to accept the glass on this basis.
Should this be acceptable to both parties, the Town and Waste Management of New York also
agree to the following:
1) The source of the fill delivered to the Town under this agreement shall be exclusively
Waste Management's NYSDEC-permitted recycling facility located at 485 Scott Avenue,
Brooklyn,NY.
2) The glass sand delivered to the Town shall possess the same chemical and
physical/geotechnical characteristics as the test loads delivered to the Town in December
1997 and as described in representative sample analyses sent to the Town(specifically, a
sieve analysis showing 99% of the sand at 3/8" or less in size, and a chemical analysis by
Accredited Laboratories, Case No. 6064), and on which basis the use of glass sand from
Waste Management was originally approved by NYSDEC in a letter to the Town dated
August 12, 1998. (see Attachment `A').
3) The glass sand must meet the guidelines for waste glass gradation and characteristics as
specified in the New York State Department of Transportation(DOT)Engineering
Bulletin(EB 94-039).
4) The Town of Southold will extract samples of glass sand from each 5,000 cubic yard
`stockpile' delivered to the Town by Waste Management, according to procedures
outlined in the letter to you from James Bunchuck of my staff dated August 18 (See
Attachment `B'). These samples will be shipped to Waste Management which shall
5) have them analyzed by a NYSDOH-certified laboratory for chemical constituents
outlined in that same letter. All costs for analysis of glass sand samples shall be borne
by Waste Management, as outlined in your letter to Mr. Bunchuck of August 25, 1999
(See Attachment `C'). Waste Management will forward the results of all glass sand
analyses to the Town and to the NYSDEC, Region 1 Office.
6) The Town of Southold will maintain unused each stockpile of 5,000 yards, separate and
secure from any other materials, until such time as NYSDEC reviews the analytic results
provided them pursuant to pararaph(4)above, and approves the use of such stockpile.
6) Notwithstanding any other procedures agreed upon for storing, sampling, and testing glass
sand delivered to the Town of Southold landfill, employees at the Town landfill will still
visually inspect each load delivered for cleanliness and other physical makeup. The Town
reserves the right to reject any load for non-compliance, in which case the load will not be
dumped,but will be removed from the landfill by Waste Management at no cost to the
Town. The Town also reserves the right to require removal or additional testing, also at no
cost to the Town, of any glass sand stockpiled at the Southold Town landfill that is later
judged, based on visual inspection,to be in apparent non-compliance,regardless of
whether the 5,000 cubic yard threshold is reached in any particular stockpile. Any fill
delivered under this agreement that is found, through testing,to be unacceptable due to
non-compliance with the chemical and/or geotechnical standards set forth in paragraph(2)
above shall be removed by Waste Management of New York within 10 business days.
7) If requested by the Town, Waste Management will agree to provide the Town with 24 hours
advance notice of the time, date, and quantity of each delivery.
8) Waste Management shall comply with all applicable federal, state, and local laws and
regulations concerning transportation of glass sand.
9) Either party may terminate this agreement, for any reason, with at least 24 hours notice
to the other party. Such termination will not absolve either party of their
responsibilities under this agreement while the agreement was in effect.
A signed copy of this letter will constitute a contract between Waste Management of New York, Inc.
and the Town of Southold. Please sign below if the above terms are acceptable, and return a copy to
me. Upon my receipt of the signed contract, deliveries of fill to the landfill may begin at any time.
You should contact Mr. Bunchuck at(516) 734-7685 to coordinate delivery schedules.
Waste Management o ,Inc.
8/27/99 Glass Sand Letter Contract
p.3
Please let me know if you have any questions.
Sincerely,
Jean W. Cochran
Supervisor
I (we)agree to the above terms for delivery of fill to the Town of Southold.
Jean W. Cochran Date
Supervisor, Town of Southold
(Type name) Date
Waste Management of New York, Inc.
f � i
hDvi rka
and
CONSULTING Bartilucci ENGINEERS
330 Crossways Park Drive,Woodbury, New York, 11797-2015
516-364-9890 s 718-460-3634 ■ Fax:516-364-9045
e-mail: db-eng@worldnet.att.net
May 11, 2000
Mr. James Bunchuck, Solid Waste Coordinator
Town of Southold
Town Hall
59095 Main Road, P.O. Box 1179
Southold,NY 11971
Re: Explosive Gas Migration to Scale House
Southold Landfill Closure
D&B No. 1314-G2
Dear Mr. Bunchuck:
As we understand it, since several thousand cubic yards of waste were removed along the
southern perimeter of the limits of waste in the vicinity of the scale house, monitoring in the
scale house (including the basement) has indicated that no detectable explosive gas is migrating
into the structure. However, as a precaution, during a recent telephone conversation you inquired
about measures to minimize the potential for hazards associated with migration of explosive gas
into the scale house.
Based on the results of the monitoring, the measures recommended at this time include
installation of a continuous explosive gas monitoring system and installation of hazardous
location sealing fittings on buried electrical and communications conduits that enter the scale
house. The continuous monitoring system should provide for detection of explosive gas in the
basement and main floor of the scale house. In addition, an uninterruptible power supply should
be provided for the gas monitoring system, the indicator displaying the gas concentration should
be clearly visible from the interior and exterior of the scale house, and the system should provide
an audible alarm if concentrations exceed the set point.
As part of the design for the closure construction, we have included a gas migration control
trench on the southern perimeter of the landfill cap. However, if in the future, explosive gas is
detected in the scale house, additional measures can be evaluated at that time. In the meantime,
if you decide to pursue the recommended measures of installing a monitoring system and sealing
the conduits, we would be pleased to provide you with any assistance you need.
A DIVISION OF WILLIAM F.COSULICH ASSOCIATES,P.C.
OVIRKA AND BARTILUCCI
Mr. James Bunchuck, Solid Waste Coordinator Page Two
Town of Southold
May 11, 2000
If you have any questions regarding this matter or require additional information, please do not
hesitate to call me.
Very truly yours,
Thomas F. Maher, P.E.
Vice President
TFM/DSGt/cmc
cc: D. Glass (D&B)
♦1314\TFMOOLTR-3 LDOC(RO1)
FEB-02-00 17 : 31 FROM: ID: 5163649045 PAGF_ 1 / 1
..l Post-It'Fax Note 7671 1#0ti ,
4. pages
To From
To Co.
Phone M Phone kip
D
f--- Fax S Fax M � +
/ y !
00,
BASIN N0. 4
CONTRACT
LIMIT LINE �� E �<<
CONI E EW. FENCE
TO EXIS INO--s ENCE
EXISTING F
TO REMAIN
O° x
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--
NOV-27-99 15 : 35 FROM: ID: S 64SO45 PAGE 1/7
r r
PRIVILEGED AND CONFIDENTIALITY NOTICE
The information in this fax is intended for the named
recipients only. It may contain privileged and confidential
Dvirka matter. If you have received this fax in error, please
notify us immediately by a collect telephone call to(516)
0 and 364-9890 and return the original to the sender by mail.
We will reimburse you for postage. Do not disclose the
Bartilucci I contents to anyone. Thank-you.
d- CONSULTING ENGINEERS
330 Crossways Park Drive,Woodbury,New York, 11797-2015
516-364-9890 •Fax:516-364-9045
D&B FAX NO: (516) 364 - 9045 DATE: November 27, 1999
COMPANY NAME: Southold
ATTENTION: Jim Bunchuck
FAX NO.: 734-7976
FROM: Dave Glass
SUBJECT: Southold Landfill JOB#:
NO. OF PAGES: Seven 7 _
(including cover sheet) —
MESSAGE:
TIM—
ENCLOSED PLEASE FIND GAS MIGRATION CONTROL, TRENCH DETAIL AND
RELATED SPECIFICATION SECTIONS.
IN CONJUNCTION WITH THE WASTE EXCAVATION WORK WHICH YOU WILL BE
DOING ALONG THE SOUTHERN PERIMETER, INSTALLATION OF A MIGRATION
CONTROL TRENCH AS SHOWN ON THE ENCLOSED SHOULD FURTHER
MINIMIZE MIGRATION OF GAS TO THE NEW LEACHING POOLS.
PLEASE REVIEW THE ENCLOSED AND WE CAN DISCUSS WHETHER THF TOWN'
WOULD BE ABLE TO INSTALL THE GAS CONTROL TRENCH IN CONJUNCTION
1V1TH THE WASTE. EXCAVATION WORK.
WE ARE STILL REVIEWING ADDITIONAL MEASURES TO CONTROL POTENTIAL
EXPLOSION HAZARDS IN THE SCALE HOUSE.
I WILL CALL,TO DISCUSS.
A DIVISION OF WILLIAM F.COSULICH ASSOCIATES,P.C.
NOV-27-99 15 : 36 FROM: 10: 5 49045 PAGE 2/7
5,-0"
TYPE I GEOTEXTILE 6" TOPSOIL
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GAS MIGRATION. TRENCH DETAIL
N.T.S.
t=0 ` 11i"OE Y ONLY.
C01`v J7` 1CTION .
SEP 1 0 1999
PROJECT No. ORAVMG No.
1314
NOV-27-99 15 : 37 FROM: ID: W649045 PAGE 3/7
6 . Gravel used for fill in the construction of the
gas migration control trenches shall be a
screened _gravel fill . The stone material shall
conform to NYSDOT Standard Specification Item No .
605-2 . 02 , Granular Filter Materials , Type 1 of
the referenced specification and shall meet the
following criteria .
Sieve Size Passing by Weight
1-inch 100
1/2-inch 30-100
1/4-inch 0-30
No. 10 0-10
No. 20 0-5
C . Exe ution
1 . e Contractor shall prepare the subgrade fortP4
tmai tenance roads to the lines and grades as
sho on the Drawings . The subgrade surface all
be co acted with an approved self-pr elled
roller eighing not less than 10 t s . All
hollows d depressions which deve op under
rolling sha be filled with accept le General
Fill materia and shall be re olled. This
process of sha 'ng, rolling and f ling shall be
repeated until no depressio develop. The
Contractor shall lace and ompact a 6-inch
(minimum) layer of ecycle concrete aggregate
(RCA) over the prepay s grade. The Contractor
shall compact the road ace using no less than
four passes of the r and shall fill and
re-roll any depress ' ns s required and as
directed by the Engi er.
2 . The stone fill or the lining f the drainway
sluice transi ons, drainage ale linings ,
drainage do chutes, around the ulvert pipe
inlet, out is and around the ripra shall be '
placed on op of the Geocomposite Drain a Layer,
as sho on the Drawings, as specified and as
direct
irer d by the Engineer . The stones sh 1 be
pla d so that the weight of the stones are
c ried by the underlying material and not by e
djacent stones . On slopes, the largest stone '
♦1314\a0927912.doc(R06) 2 . 11-4 ,
NOV-27-99 15 : 39 FROM: 0 ID: I3G49O45 PAGE 4/7
ch side and top. The stone filling shall
car ully placed and packed by hand so tha he
CHDPE a is not compressed or deforme . The
top patch hall then be wire laced the top
surface of t reno mattress to ieve proper
alignment and a eat, compact earance. The
lacing shall be in a same nner as described
herein for assembly.
Where shown on the D ings otherwise directed
by the Engineer, ish shall be ut, folded and
wired together o suit existing si conditions .
Mesh must b leanly cut and surplus m cut out
completel or folded back and neatly wir to an
adjace Reno mattress face. Cut edges of esh
sh be securely laced together with lacing w-
the manner described above .
6 . The Contractor shall install the screened gravel
fill in the gas migration trenches . The gravel
placed in the gas migration trench shall be
placed in 24-inch layers from the bottom of the
trench to within 6-inches of the surface.
Geotextile Type 1 shall be installed along the
sides of the gas migration trench before the
gravel fill is placed and on top of the gravel
fill when the filling is complete as shown on the
drawings, as specified and as directed by the
Engineer . The gravel shall be placed in a manner
that will produce a reasonably well graded mass
of stone.
layer in the construction si
pad shall be in on the Drawings,
ie and as directed by==M!;
4131a\aO827912.dcc(RO6) 2 . 11-7
NOV-27-99 15: 39 FROM: ID:03649045 PAGE 5/7
C . No geotextile shall be shipped until the
affidavit is submitted to the Engineer.
I' -----�
C . materials
I1 . Type I Geotextile
a. The geotextile shall be an 8 oz . /sq. yd.
continuous filament polyester or
polypropylene nonwoven needlepunched fabric .
The fabric shall be inert to commonly
1 encountered chemicals, biological
' degradation, hydro-carbons, acids, alkalies
and mildew. The fabric shall be resistant
to rot, ultraviolet light, insects and
rodents .
b. The polyester or polypropylene filaments
' shall be formed into a stable network such
that the filaments retain their relative
position.
C . The manufacturer shall provide
certifications that each roll (identified by
roll number) of geotextile conforms to the
requirements of these specifications . The
certifications shall be submitted to and
reviewed by the Engineer prior to the
installation of the material .
d. The geotextile polymer composition shall be
at least 95% polypropylene or polyester by
weight .
e. The minimum roll width shall be 15 feet .
1 The roll length shall be maximized in order
to minimize seams .
ff . The Type I Geotextile shall be TG700 as
manufactured by Evergreen Technologies,
Inc . , Hoechst Celanese, 801 Geotex as
manufactured by Synthetic Industries or
approved equal .
g. The Type I Geotextile shall conform to the
properties listed in Table 4 . 1-1 .
•1314/kC920902.doc(R04) 4 . 1-5
NOV-•27-99 15: 39 FROM: 0 ID: *649045 PAGE 6/7
Table 4.1-1
TYPE I GROTEXTILE
Fabric PropertY Test Method unit specified Qualifier(l)
Value
Fabric Weight ASTM D5261 oz/sq yd 7.9 MARV
Thickness, t ASTM D5199 mils 85 MARV
Grab Strength(2) ASTM D4632 lbs 210 MARV
Grab Elongationf21 ASTM D4632 % 50 MARV
Trapezoid Tear ASTM D4533 lbs 80 MARV
Strength12)
Puncture ASTM D4833 lbs 100 MARV
Resistance
Mullen Burst ASTM D3786 psi 320 MARV
Strength
Water Flow Rate ASTM D4491 gpm/sq ft 90 MARV
Permittivity ASTM D4491 sec'1 1.2 MARV
Permeability ASTM D4491 cm/sec 0.3 MARV
Apparent Opening ASTM D4751 sieve size 70 MARV
Size (AOS) mm 0.212
UV Resistance ASTM D4355 % strength 70 MARV
retained
pH Resistance 2-13 Range
Notes:
(1) MARV - Minimum Average Roll Value.
(2) Values in the weakest principal direction.
•1314/k0820902.doc(ROU 4 . 1-7
,NOV-27-99 15:40 FROM: if ID: 510649045 PAGE 7/7
o
2 . -Bek @N +reI1 €--- eetoevekiIe dei imp
-tell---ekesely -ensawe---the--manmiaemirer, a none?
azle - if+�ne�e �aeT-and,
-ereeeewe
3 . Geotextile shall be protected from ultraviolet
light exposure, precipitation or other
inundation, mud, dirt, dust, puncture, cutting or
any other damaging or deleterious conditions .
4 . i--g�ava eke all--babe r---pend
i
5 . Rolls shall be stored in a manner which protects
them from the elements .
6 . The Contractor shall not use any hooks, tongs or
other sharp tools or instruments for handling the
rolls . The Contractor shall utilize non-damaging
slings or a pole which extends a minimum of 1
foot beyond each end of the roll to unload or
handle individual rolls .
7 . The geotextiles shall not be dragged along the
ground.
B .
.., -Alt- 4-1, tJfp_-. — ___--ill-bak %ien p see--der e
r
9 . geotextile materials which have b �
appro properly handled and stored, for
which acce a roll certificati ave been
received and aPpr shall be talled.
10 . The Contractor s asst. the Engineer in
obtaining co ance samples fro a material
at the a of placement . A conforman ample
s measure 3 feet in roll length by the w
♦1314/k0820902.doc(R04) 4 . 1-10
MBIENT AIR MONITORING I 0`v
DINT LOCATION
REATER THAN 25X LOWER �\
XPLOSIVE LIMIT (LEL) ' FORM AREA
BORROW
14 Q
REA OF POTENTIAL EXCEEDANCE
F 25X LEL BASED ON ONE ROUND 14A
F OVA READINGS >1000pm
)ASHED WHERE INFERRED I 1148 0
x
4 12 /12C 12D 12E "F 1 1 3A 13B 14C
118
11A 1�y�11E 11�/ 12 /
I ..._ 1 _ 15A I r
GER 1`� / 158 METHANE VENTING
TRENCH
,S100 FT. ,
1 � i r5C �
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1 �/ LIMITS OF I � /
10 WASTE ELEVATE
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/ I
XIMATELY AREA 15�
3FT. I � I 5 �
8C I I 6
s COMMERCIAL BI—LEVEL DROP—OFF
STATION FOR RECYCLABLES
19 OVERHEAD
ELECT
LINES
6
/ 6\\` Al �� 20•
78 �
3A 3 A HOUSEHOLD HAZARDOUS WASTE
7A -'��'�8 F CONTAINMENT FACILITY
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----�')� "ORTM 0 300 600
13
:/09/98
TOWN OF SOUTHOLD - SOUTHOLD LANDFILL
CLOSURE INVESTIGATION
and Bartilucci EXTENT OF SOIL GAS GREATER THAN 257o OF THE
ng
fnW'"iam F. Cosulich Associates. P.C. LOWER EXPLOSIVE LIMIT FIGUR' 4-24
MONITORING POINT LOCATION Q`'❑
AMBIENT AIR MONITORING \\\
POINT LOCATION 0
GREATER THAN 25X LOWER IFORMER BORROW
EXPLOSIVE LIMIT (LEL) II AREA 14
AREA OF POTENTIAL EXCEEDANCE II �j 14A
OF 25X LEL BASED ON ONE ROUND
OF OVA READINGS >1000 pm �� 114B 0
(DASHED WHERE INFERRED
38
4 12 1 2C 12D 12E I
12F 1. 13A 1
• 14C
II I
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METHANE VENTING �n
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VENGER f
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APPROXIMATE I 15D 4146
/ LIMITS OF I
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COMMERCIAL BI-LEVEL DROP-OFF
a y" STATION FOR RECYCLABLES
I � 19 ELECTREIACD
LINES
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78 i A3 A HOUSEHOLD HAZARDOUS WASTE
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7A o 7 22
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A4
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STORAGE _� 2STATION ION
GARAGE '�I� 34 SE
48
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1314 11
1314-03 _—
ms-09/09/96
TOWN OF SOUTHOLD — SOUTHOLD LANDFILL
CLOSURE INVESTIGATION
ivirka and Bartitucci EXTENT OF SOIL GAS GREATER THAT 25% OF THE FIGURE "
`ons�+�n9 Enginsen LOWER EXPLOSIVE LIM
Division of William F. Cosulich Associates. P.C.
.MBIENT AIR MONITORING II u\1
'DINT LOCATION
REATER THAN 25% LOWER Il MER BORROW \
XPLOSIVE LIMIT (LEL) II ) FORMER
14
.REA OF POTENTIAL EXCEEDANCE �r /
)F 25% LEL BASED ON ONE ROUND I 14A
)F OVA READINGS >1000pm
DASI4ED WHERE INFERRED ' 1148
4 4 ,2 I12 C 1 2b 1 2E r1�F 13 13A 130
I o
^� • 14C
1B „C 15A i 1 E „y +�
11A
AGER 1`� ~ 158 METHANE VENTING
TRENCH
4S 100 FT. ,, I r5C
1 /�APPROXIM OF ( 15D d46 ED / --�
LIMITS 0
10; WASTE C
r ( ELEVATED 15E
� LANDFILL
AREA 15
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COMMERCIAL 81–LEVEL DROP–OFF
8A STATION FOR RECYCLABLES
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8 \ Al �� 20
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GARAGE I 34 II (SCALE HOUSE
29 Q
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I �y 3 '� (COUN
NORTH ROAD
I 0 300 600
-03
09/09/00 - - ---
TOWN OF SOUTHOLD -- SOUTHOLD LANDFILL
CLOSURE INVESTIGATION
<aand Bartilucci EXTENT OF SOIL GAS GREATER THAN 25% OF THE
,hi Enillneem LOWER EXPLOSIVE LIMIT FIGURE 4-2-
+ision of William F. Cosulich Associates, P.C.
R 'C s
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w SENT BY:Xerox Telecopiel&20 ;12- 3-7? : 1 :56PM X163648675- 7347976;# 1
d1Dvirka
and
Q Bartilucci
CONSULTING ENGINEERS
330 Crossways Park Drive,Woodbury,New York, 11797.2015
518-364-9890 a Fax:516-384.9045
TElEFU NO: (511) 804-SOU DATE '
COMPANY NAME: TQW K J0 S,a u�c
XMNTION: I'm �v hGH v c tc
FAX NL: 734 — III
FROM: Daysd 0w1-6LxOViLI\ '
SUBJECT:
0.OF PAGES:
(including cover sheet)
MESSAGE:
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fe-cord re adetkjr o g;ve w�c- call
THANK YOU:
A DIVISION OF WILLIAM F.COSULICW ASSOCIATES,P.C.
SENT BY:Xerox Telecopiero0 ;12- 3-7? ; 1 :57PM ; 03648675-+ 7347976;it 2
AND DESIGNATION
• TEMPORARY EXPLOSIVE GAS ) FORMER BORROW
MONITORING POINT LOCATION II AREA 1
J AMBIENT AIR MONITORINGI ��
POINT LOCATION 'n
1148 0
43 12 12C 12D 12E gF 13 13A 138 114C
1 +.-� rte► r^' �
11®
iic
FRMSCAVENGER 1�� 1 METHANE VEN I
TRENCH
LATE
LAG
100 F1`.
//APPROXIMATE ( � /
10�
LIMITSOF 1 '
ELEVATED 13
1 LANDFILL
/ � ( AREA
APPROXIMATELY
300 FT. `
1 1
r� �1
ec
8 •SO 5
ERCIAL 81— L DROP—OFF
` TATION FOR RECY BLES
1 �R
19 LJNES IC _
�B
1Q\N` Al �� 20
4 1 - -
3A 3 A HOUSEHO HAZA D US WASTE
7A .,��,,,..�„4�,•+d® ` F CONTAINM N1' FACI
+rr►��,�,. 2
232
WASTE 01L
1A`
STORAGE TANKS
`2 COLLECTION CENTER
ftw . I !t
ME O 3I 29 WEIGHING STATION
34 (SCALE HODS
2. Q y
2 '1 (COUNTY ROAD 48 C� ❑
cn
TH ROAD
N
� 0--- - 300.
1314
131 -11
TOWN OF SOUTHOLD - SOUTHOLD LANDFILL
CLOSURE INVESTIGATION
Dvirka and Bortiiucci EXPLOSIVE GAS MONITORING POINT LOCATIONS
E
AA DMOM of Whom F. Cosufiich ANocIct". P.C.