J .
United States
Environmental Protection
Agency
Office of
Emergency and
Remedial Response
EP AlRODIR05-931229
June 1993
PB94-964106
&EPA
Superfund
Record 01 Decision:
Woodstock Municipal
Landfill, IL
u . ~. Environmental Protection Agency
Beglo~ III, /:1azardous Waste
fechmcar Information Center
8~ 1 Cl1es~nut Street, 9th Floor
P alphl
Hazardous Waste Collection
Information Resource Center
US EPA Region 3
Philadelphia. PA 19107
EP A Report Collection
Information Resource Center
US EP A Region 3
Philadelphia, PA 19107
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50272.101
REPORTDOCUMENTAll0N 11. REPORT NO.
PAGE EPA/ROD/R05-93/229
~
3. Recipient's Accaalon No.
4.
TItle and SubtlU8
SUPERFUND RECORD OF DECISION
Woodstock Municipal Landfill, IL
First Remedial Action - Final
A~hor(a)
5.
Allport Date
06/30/93
6.
7.
8.
Performing Organization Allpl. No.
9.
Performing Organization Name and Add,..
10
Project TuklWortc Unit No.
11. Contract(C) or Grant(G) No.
(C)
(G)
12. SponsorIng Organization Name and Add.....
U.S. Environmental Protection
401 M Street, S.W.
Washington, D.C. 20460
13. Type o' Report & PwIocI eover8d
Agency
800/800
14.
15. Supplementary Nol.
PB94-964l06
16. Abstract (Umlt: 200 words)
The Woodstock Municipal Landfill site is an inactive municipal and industrial landfill
located on the south side of Woodstock, Illinois. Land use in the area is mixed
residential, agricultural, commercial, and light industrial, with wetlands adjacent to
the east and south of the site. In addition, the Kishwaukee River runs along the
southwestern perimeter of t~e landfill. The majority of residents in the City of-
Woodstock obtain their water from a municipal supply system. Ground water beneath the
site either is being used currently as a drinking water source or could potentially be
used as a drinking water source in the future. The landfill is currently owned by the
City of Woodstock, and has had a number of different owners between 1935, when it was
first used as a trash dump and open burning area, and 1980, when it was closed. From
1940 to 1958, the site was owned by a private citizen and used as a local trash dump
and open burning area. From 1958 to 1968, the site was leased by the City of Woodstock
and was used for the disposal of household and municipal solid waste and various
industrial solid wastes, including waste paint, coating materials, plating wastes,
solvents, waste metals, inks, and drummed material including PCBs.. Additionally,
Woodstock Die Casting Inc. disposed of approximately 7,200 yd3 of sludge at the
(See Attached .Page)
17. Document Analysis L Dascrlptora
Record of Decision - Woodstock Municipal Landfill, IL
First Remedial Action - Final
Contaminated Media: soil, sediment, debris, gw
Key Contaminants: VOCs (benzene, toluene, xylenes), other. organics (PAHs), metals
(arsenic, chromium, lead)
b.
1cf8nt11le1'8lOpan-Ended Terms
Co
COSATI FleldIGroup
18. Availability Statement
19. Security Class (This Report)
None
3). Security Class (ThIs Page)
None
21. No.o'Pagn
166
22. Pr1c8
(Sea ANSI-Z39.18)
SH/nstrvctions on R..,-
OP'TJONAL FORM 272 (4077)
(Formerly NTl5-35)
Department o' Commerce
-------
EPA/ROD/R05-93/229
Woodstock Municipal Landfill, IL
First Remedial Action - Final
Abstract (Continued)
landfill. From 1983 to 1988, municipal sewage sludge was landfarmed on the site. In 1968,
the City purchased the site and continued disposal activities until 1975, when they
covered the area with fill material. In 1988, an EPA sampling investigation revealed that
residential wells located downgradient of the landfill were contaminated with arsenic,
selenium, and thallium in excess of SDWA MCLs. This ROD addresses a final remedy for the
contaminated soil, sediment, debris, and ground water at the landfill. The primary
contaminants of concern affecting the soil, sed~ent, debris, and ground water are VOCs,
including benzene, toluene, and xylenes; other organics, including PAHs; and metals,
including arsenic, chromium, and lead.
The selected remedial action for this site includes excavating and consolidating any
contaminated soil and sed~ent on the landfill surface, followed by capping the landfill
with a geosynthetic membrane and bentonite clay layer, drainage layer, and topsoil;
installing ground water extraction wells in the area of the vinyl chloride contamination
and pumping the water to an offsite POTW, or if the pretreatment standards for the POTW .
are exceeded, to an onsite treatment facility; designing a surface water control system to
limit erosion of the landfill cover and monitoring surface water runoff at distinct
discharge points, as well as monitoring the sedimentation basin and wetlands water
quality; designing the grading layer to route landfill gases to a venting system and
sealing the leachate seeps; monitoring ground water; and implementing institutional
controls, including deed, ground water, and land use restrictions. The estimated present
worth cost for this remedial action is $8,681,000, which includes an estimated annual O&M
cost of $129,000 for 30 years.
PERFORMANCE STANDARDS OR GOALS:
No chemical-specific soil, debris, or sed~ent cleanup goals are provided. The
chemical-specific ground water cleanup goal is vinyl chloride 2 ug/l and is based on SDWA
MCLs.
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RECORD OF DECISION
SELECTED REMEDIAL ALTERNATIVE
DECLARATION
SITE NAME AND LOCATION
Woodstock Municipal Landfill
Woodstock, Illinois
STATEMENT OF BASIS AND PURPOSE
This decision document represents the United States Environmental
Protection Agency's (U.S. EPA) selected remedial action for the
Woodstock Municipal Landfill (Woodstock) site located in
Woodstock, Illinois. This decision document was developed in
accordance with the Comprehensive Environmental Response,
Compensation and Liability Act of 1980 (CERCLA), as amended by
the Superfund Amendments and Reauthorization Act of 1986 (SARA),
and to the extent practicable, with the National Oil and
Hazardous Substances Contingency Plan (NCP). This decision is
based on the Administrative Record for this site.
The State of Illinois is expected to concur with the selected
remedy.
ASSESSMENT OF THE SITE
Actual or threatened releases of hazardous substances from the
site, if not addressed by implementing the response action
selected in this Record of Decision (ROD), may present an
imminent and substantial endangerment to public health, welfare,
or the environment.
DESCRIPTION OF THE REMEDY
This remedy is intended to be the final action for the site. The
remedy addresses all contaminated media and includes:
contaminated soil, sediment, and groundwater, landfilled wastes,
leachate generation and emission of landfill gases.
The major components of the selected remedy include:
.
Excavation and consolidation of contaminated sedimen~s
and sludges under the landfill cap;
.
Installation and maintenance of a geosynthetic landfill
cap in compliance with Illinois Administrative Code
(IAC) Title 35, Subtitle G, Chapter 1, Subchapter
i: Solid Waste and Special Waste Hauling, Part 811.314;
.
Installation and maintenance of a landfill gas venting
system that is compatible with the type of cap
-------
specified in this Record of Decision;
*
Instal:ation and operation of a groundwater extraction,
treatm~nt, and discharge system;
*
Development and implementation of a comprehensive
monitoring program to ensure the effectiveness of the
remedy;
*
Mitigation of wetland areas where contaminated sediment
removal occurs;
*
Mitigation of wetland damage or loss during or after
remedial activities are complete;
*
Development and implementation of a surface water and
sedimentation control system;
*
Implementation of institutional con~rols to limit land
and groundwater use.
STATUTORY DETERMINATIONS
The selected remedy is protective of human health and the
environment, complies with Federal and State requirements that
are legally applicable or relevant and appropriate to the
remedial action, and is cost-effective. This remedy utilizes
permanent solutions and alternative trE~~ment technologies to the
maximum extent practicable and satisfiE the statutory preference
for remedies which employ treatment the =educes toxicity,
mobility, or volume as a principal eler-" _:.t.
Because this remedy may result in hazardous substances remaining
on-site above health-based levels, a review will be conducted at
least e ery five years after commencement of the remedial action
to ens re that the remedy continues to provide adequate
prote tion of h health and the environment.
~h3.
, (
Date
j
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SUMMARY OF REMEDIAL ALTERNATIVE SELECTION
WOODSTOCK MUNICIPAL LANDFILL
WOODSTOCK, ILLINOIS
1.
Site Name, Location and Description
The Woodstock Municipal Landfill site is located on the
south side of the city of Woodstock, Illinois, a
municipality with a population of approximately 14,350
residents. The site is located south of Davis Road,
southwest of the intersection of U.S. Route 14 and Illinois
Route 47 and is shown on Figure 1. The coordinates for the
site are northeast quarter of Section 17, Township 44 North,
Range 7 East (NE 1/4, Se 17, T44N, R7E).
The land surrounding the Woodstock site is a mixture of
residential, agricultural, wetlands, commercial, and light
industrial use. Land use immediately north of the site is
primarily residential and agricultural. Land use west of
the site is semiagricultural with much of the land currently
classified as a wetland. Wetlands are located adjacent to
the site on the east. Kishwaukee River runs south along the
southwestern perimeter of the site. The City of Woodstock
Wastewater Treatment Plant and additional wetlands are also
located south of the site.
The site geology consists of a complex sequence of
unconsolidated glacial deposits which are approximately 200
feet thick. These deposits have been divided into four
units; an upper sand and gravel aquifer, an intermediate
clay till member, a lower clay till member, and a sand unit
which overlies bedrock comprised of dolomite and shale. The
glacial and bedrock aquifers underlying the site are
considered to be Class I by the State of Illinois. Class I
aquifers include groundwater which is either currently being
used or has the potential to be used as a drinking water
source. Surface water runoff is generally to the west and
south and is confined by drainage to the wetlands and
subsequent infiltration or overland flow into Kishwaukee
River.
The nearest residents to the site are located approximately
500 feet north of the site. The nearest existing
residential well which may potentially be impacted by the
contaminated groundwater if further migration occurs is
located approximately 2500 feet southwest of the site.
Based on data collected during the remedial investigation,
groundwater contamination has not migrated to the local
residential wells used for drinking water. The majority of
the residents in the City of Woodstock are provided water
through a municipal water supply system. This system is not
considered to be threatened by the site.
-------
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FIGURE 1
SITE LOCATION MAP
WOODSTOCK MUNICIPAL LANDFILL
WOODSTOCK, IL
-------
II.
2
Site Historv and Enforcement Activities
The landfill had a number of different owners between 1935,
when it was first used as a trash dump and open burning
area, and when it was covered and classified as closed by
the IEPA in October 1980. The current owner of the landfill
property is the City of Woodstock. Other properties which
are considered part of the site are under private ownership.
From approximately 1940 until leased to Woodstock in 1958,
the site was used as a local trash dump and open burning
area by william Gaulke. The site was used by the City under
a lease agreement with Mr. Gaulke as a household garbage and
municipal landfill from 1958 until its acquisition by the
City in 1968. Following acquisition of the property, the
property was used for the disposal of household and
municipal solid waste and various industrial solid wastes
including waste paint and coating materials, plating wastes,
solvents, waste metals, inks and drummed material including
polychlorinated biphenyls. In addition, approximately 7200
cubic yards of sludge generated by Woodstock Die Casting
Inc., an Allied Signal subsidiary was also disposed of at
the landfill.
The IEPA filed a complaint against the City of Woodstock in
1972 regarding operation of the landfill. The Illinois
Pollution Control Board (IPCB) issued an opinion that
evidence substantiated charges of open dumping, liquid
deposition without approval, failure to follow set
guidelines, and operating without a permit. The City of
Woodstock was ordered to cease and desist all violations,
obtain the necessary permits, and was fined for its actions.
During this same time period, IEPA requested the
installation of a leachate collection system to address
releases from the landfill. However, no system was
installed and a waiver was granted by the IPCB based on the
City of Woodstock's stated intent to close the landfill in
the near future and because the leachate did not violate
surface water standards at the time. The City discontinued
disposal activities at the site in 1975 and closed the
landfill by covering it with fill material. Numerous
inspections were conducted at the site by IEPA from 1975-
1980. IEPA continually notified the city during this time
that the landfill was indeed no longer accepting waste and
was considered closed, but the final cover was deficient.
In 1980, the IEPA classified the site as closed and covered.
In 1983, the City was granted a permit from the IEPA to
landfarm municipal sewage sludge at the site. A second
permit was issued by the IEPA in July 1988, but sludge
application was discontinued prior to that date, so the
later permit has not been used.
-------
3
During a July 1988 sampling investigation by the Technical
Assistance Team (a USEPA contractqr tasked to do site
investigations), residential wells located downgradient of
the landfill were sampled and found to contain arsenic,
selenium, and thallium in excess of the Safe Drinking Water
Act maximum drinking water level's. A subsequent sampling
investigation in December 1988 again detected these
substances in the same wells, but the concentrations did not
exceed the regulatory criteria.
Based on the results of U.S. EPA and IEPA investigations and
taking into account such factors as populations at risk, the
potential of hazardous substances being present; the
potential for contamination of drinking water supplies and
the potential destruction of sensitive ecosystems, the site
was proposed to be placed on the National Priorities List in
June 1988. The site was placed on the National Priorities
List in October 1989. A consent order to conduct an RI/FS
was agreed to by Allied Signal and the City of Woodstock in
September 1989.
III. Hiqhliqhts of Community Particioation
Compliance with the public participation requirements of
Section 113 (k) (2) (B) (i-v) of CERCLA/SARA, have been
achieved for the Woodstock site by:
A press release was issued" in JU~2 1990 announcing
a public "Remedial Investigation/Feasibility Study
(RI/FS) kick-off" meeting to be held to inform the
community as to U.S. EPA plans;
The public "RI/FS kick-off" meeting was held in
June 1990, announcing the initiation of the RI/FS;
A fact sheet was developed and distributed in
conjunction with the June 1990 meeting;
A site information repository was established at
the Woodstock Public Library to allow local access
to site-related documents;
A fact sheet was sent to all persons or
organizations on the community relations mailing
list in October 1992 updating them on the progress
of the project;
An Administrative Record has been compiled,
including the RI, Baseline Risk Assessment, FS,
and other documents, and has been placed in the
site information repository;
-------
IV.
4
A formal advertisement announcing the commencement
of the public comment period, the availability of
the proposed plan, and the time and place of the
public meeting was placed in the Northwest Herald
on April 7, 1993. The Herald is a major local
paper of general circulation;
The Proposed Plan for remedial action was released
for public comment and placed intQ the
Administrative Record on April 9, 1993;
A thirty (30) day comment period was established
and scheduled to end on May 10, 1993;
A public meeting was held on April 28, 1993, at
the Woodstock Public Library at which u.s. EPA and
IEPA presented the Proposed Plan to the community
and received verbal comments. A transcript was
kept of the public meeting and was made available
to the public and placed in the Administrative
Record and site repositories;
A fact sheet was developed and distributed in
conjunction with the April 28, 1993 meeting;
u.s. EPA granted a thirty (30) day extension of
the public comment period on April 28, 1993,
extending the closing date to June 9, 1993;
An advertisement was placed in the local newspaper
on May 12 and May 13, 1993, announcing the
extension of the public comment period to June 9,
1993;
Three public availability meetings were held
on June 2, 1993 at the Woodstock Public Library
to address community concerns dealing with the
risks posed by the site as well as to answer
additional concerns with the proposed remedy:
u.s. EPA has received oral and written comments
regarding the RIfFS, Baseline Risk Assessment, and
the Proposed Plan. Comments have been addressed
in the attached Responsiveness Summary.
SCODe and Role of the Selected Remedv
This ROD addresses remediation of the contaminated surface
soil, sediments, and groundwater and addresses leachate
which is being generated and is discharging from the
landfill. The contaminants found in these media represent
-------
5
the principal threat from the Woodstock site. The
generation of leachate presents a threat as a continuous
contaminant source to groundwater, surface water and to the
wetlands surrounding the site. In addition, a direct
contact threat exists from exposure to surface soils and
leachate. The primary purpose of this remedy is twofold; 1)
to restore the contaminated groundwater to an acceptable
level that will allow for its unrestricted use and 2) to cap
the landfill, thereby minimizing the generation of leachate
and eliminating the risk posed by the surface soils and
sediments.
V.
Summary of Site Characteristics
The remedial investigation was conducted by the PRP's
contractor, Warzyn, and was initiated in July 1990. The
investigation was completed in June 1992 when the Final
Remedial Investigation Report was issued. The remedial
investigation identified the types of contaminants that are
migrating from the landfill, and assessed the potential
impact of contaminant migration on human health and the
environment. The assessment of the landfill was
accomplished by conducting three phases of field work. The
purpose of phase I was to gather information on the general
nature of the site, such as the geology and hydrogeology,
and to identify and quantify the nature of any potential
impact at or surrounding the site. The purpose of phase II
was to complete the understanding of the site
characteristics. This included delineation of the extent to
which contamination was released from the site and the
interactions between groundwater, surface water and
leachate. The assessment was completed with the phase III
investigation which included test pit excavation, waste
sampling, additional soil sampling and further refine~ent of
the groundwater flow regime of the site. Figures 2 and 3
depict the locations of the various samples which were
collected during these phases of work. During the course of
these phases of fieldwork, data were obtained from sampling
residential wells, monitoring and leachate wells, surface
and subsurface soils, surface water and sediment.
The following is a brief overview of the nature and extent
of the contamination found during the investigation:
Landfill Gas Characteristics
Gas samples were collected from leachate wells with the
highest rate of gas flow (LW-3 and LW-4). Volatile organic
compounds (VOCs) were detected and included Freon 114,
chloroethane, benzene, toluene, chlorobenzene, ethylbenzene,
4-ethyl toluene, l,3,S-trimethylbenzene, 1,2,4-
-------
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L.£GEND
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I LEACHATE WELL.
STAFF GUAGE
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-------
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LEGEND
* SURFACE WATER
. SEDIMENT
. SURFACE SOIL
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SCALE IN FEET
500
1000
.
FIGURE 3
SURFACE WATER, SEDIMENT, AND
SURFACE SOIL SAMPLE LOCATION MAP
WOODSTOCK MUNICIPAL LANDFILL
WOODSTOCK, IL
-------
6
trimethylbenzene, and xylene. Concentrations of these
compounds ranged from 48 to 470 ppb.
Landfill Leachate Characteristics
Two rounds of leachate samples were collected from each of
the five leachate wells. Analysis of these samples detected
the presence of VOCs including benzene, chlorobenzene, 1,2
dichloroethene, toluene, and xylene ranging in concentration
from 1 to 16 ppb. Naphthalene, a semi-volatile compound,
was also detected at concentrations ranging from 6 to 34
ppb. In addition, several tentatively identified VOCs and
semi-volatile organic compounds (SVOCs) were also identified
and ranged in concentration from 3-48 ppb. A number of
metals including arsenic, antimony, barium, beryllium,
cadmium, cobalt, copper, chromium, iron, lead, magnesium,
mercury, nickel, selenium, silver, vanadium, and zinc were
also detected and ranged in concentration from 1 ppb to 185
ppm. Metals which were detected that exceeded primary
drinking water standards include arsenic (ranged from 77-102
ppb with 50 ppb as the standard), barium (810-10,800 ppb,
standard is 1000 ppb), chromium (86-1400 ppb, standard is 50
ppb), copper (497-3070, standard is 1300 ppb), lead (150-
18,000 ppb, standard is IS ppb), mercury (2.2-3.9 ppb,
standard is 2 ppb), and nickel (1070-15,000 ppb, standard is
100 ppb). During the installation of the leachate wells, it
was noted that infiltration of water was causing a mounding
effect to occur, generating a large volume of leachate that
subsequently discharges from the landfill.
Surface Soil Characteristics
Surface soil samples were collected and were found to be
contaminated with numerous SVOCs, many of which were
tentatively identified but were classified as unknown.
SVOCs which were identified include phenanthrene, di-n-
butylphthalate" fluoranthene, pyrene, butylbenzlphthalate,
benzo(a) anthracene, chrysene, benzo(a)pyrene,
benzo(g,h,i)perylene, benzo(b)fluoranthene,
benzo(k)fluoranthene, and 4-chloroaniline. Concentrations
of the known and tentatively identified SVOCs range from 43-
23000 ppb. In addition, numerous inorganic compounds were
also detected including arsenic, barium, cadmium, chromi~,
copper, iron, lead, magnesium, manganese, mercury, nickel,
selenium, silver, and zinc. Concentrations of these
compounds range from 0.07-34000 ppm.
-
Waste Characteristics
Five test pits were excavated in areas identified as
possible drum disposal locations. One test pit yielded an
intact drum containing polychlorinated biphenols (PCBs),
-------
7
acetone, 4 methyl-2-pentanone, and toluene. In addition,
several crushed drum lids and/or drum fragments were also
discovered during this activity. Other test pits located
crushed drums which no longer contained waste product(s).
Groundwater Characteristics
A total of 17 monitoring wells were installed at the site
and each of these wells was sampled twice, with the
exception of MW-11, which was installed and sampled at the
end of the scheduled fieldwork. Inorganic contaminants were
detected including cyanide, lead, zinc, nickel, . iron,
manganese, and magnesium. Concentrations of these
contaminants ranged from 3-1750 ppb. VOCs were also
detected including benzene, toluen~. chlorobenzene, 1,2
dichloroethene, and vinyl c: ~0rid~. Concentrations of VOCs
ran£=d from 2-21 ppb. Vinyl ~hloride, which was detected in
the upper aquifer in monitoring wells MW-4D and MW-8,
exceeded :he maximum contaminant level (MCL) of 2 ppb for
this contaminant. The vinyl chloride plume is shown on
Figure 4. In addition, secondary drinking water standards
were exceeded for iron, manganese, chloride, and total
dissolved solids.
Surface Water Characteristics
A total of four surface water samples were collected from
locations near the landfill in Kishwaukee River. Analysis of
these samples identified the presence of arsenic, barium,
copper, iron, lead, manqanese, nickel and zinc.
Concentrations of these 'ntaminants ':anged from '-.4 - 32,200
ppb. The levels of iro!. ;tected ir. :hese sampl exceeded
the ambient water qualit- ;riteria fer this compo~nd.
Sediment Characteristics
Sediment samples collected from the surrounding wetlands and
Kishwaukee River contained one VOC, toluene, at
concentrations ranging from 7-92 ppb. In addition, arsenic,
barium, iron, lead, magnesium, manganese, mercury, vanadium,
selenium, copper, nickel, zinc, and chromium were also
detected ranging in concentration from 0.15-67000 ppm.
-.
The data tables which identify the media that was sampled,
the contaminant(s) identified in that media, and the
respective concentrations have been attached as an appendix
to this document.
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PRESENCE IN UPPER
AQUIFER
('
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SCALE IN FEET
500
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.
FIGURE 4
ESTIMATED AREA OF VINYL CHLORIDE
PRESENCE IN THE WATER TABLE AQUIFER
WOODSTOCK MUNICIPAL LANDFILL
WOODSTOCK. IL
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8
The key -~nclusions which may be surmised from this data are
as follc~3:
Groundwater contamination was detected in the upper
aquifer immediately southwest and downgradient of the
landfill. The contaminant of concern, vinyl chloride,
was detected at concentrations that exceed the maximum
contaminant level of 2 ppb (e.g. the maximum
permissible level) for this compound.
Contamination was detected in leachate gas samples and
in leachate groundwater samples collected from wells on
the landfill. The contaminants included volatile
organics such as benzene, ethylbenzene, toluene and
xylene. In addition, inorganic contaminants such as
arsenic, barium, chromium, lead and mercury were also
detected in excess of regulatory criteria. Leachate is
also identified as the source of contamination that is
adversely affecting the groundwater, surface water and
sediments at the site.
Contamination was detected in surface soils, surface
water, and sediments at the site. These three media
were contaminated with a wide range of VOCs, SVOCs, and
inorganic compounds.
Leachate generation, if not controlled, will continue
to cause further releases to the impacted media and
surrounding wetlands and result in further adverse
environmental impacts. While the wetlands are
currently limiting the full impact of the landfill
releases to the environment through attenuation, the
capacity and capability of the wetlands to function in
such a manner is limited.
VI.
Summary of Site Risks
Risks to Human Health
A major goal of the RI was to assess potential risks to
public health and the environment if the Woodstock site is
not remediated. The assessment of impacts to human health
is called the Baseline Risk Assessment (BLRA). Using
information about what contaminants are present at the site,
as well as the concentrations, quantities, locations and
ability of the contaminants to migrate, a BLRA was developed
to determine what, if any, risks are posed by the site and
if remedial action is warranted.
Separate calculations are made for those compounds that can
cause cancer and for those that can have other health
-------
9
effects. For the compounds that can cause cancer
(carcinogens), risks are estimated as the additional
possibility of developing cancer due to exposure to the
compounds. For the non-cancer causing compounds
(noncarcinogens), a risk number called the hazard index
is calculated so that if the risk is less than or equal
I, no adverse health effects would be expected. If the
is greater than I, adverse health effects are possible.
The BLRA indicates that the site as it now exists, may pose
an unacceptable cancer risk (CR) of 5 x 10~ or CR = 5 x 10~)
to trespassers (children/adolescents playing on~site)
through exposure to surface soils. This exposure may occur
through ingestion or dermal contact with polyaromatic
hydrocarbons (PARs) which are present in the contaminated
surface soil. An additional physical hazard is currently
posed to children by the debris piles and miscellaneous
debris located on the site.
(HI)
to
risk
The BLRA also identified unacceptable cancer and non-cancer
risks posed by the site under future land-use scenarios. As
mentioned above under the current land use conditions,
exposure to PARs in the surface soil poses an unacceptable
level of cancer risk to trespassers. In addition, under the
potential future use scenario of the site being used as a
park or recycling center, consumption of leachate from an
on-site well was estimated to pose a potential non-cancer
(hazard index of 10 or HI = 10) and cancer (CR = 4 x 104)
risk to these park users. The primary chemicals that posed
a non-cancer risk due to leachate consumption were cadmium,
cobalt, copper, lead, nickel and zinc. The primary
chemicals that posed a cancer risk were arsenic and
beryllium. Another potential health risk would also exist
if a well was placed in or near the area contaminated with
vinyl chloride. In this scenario, an unacceptable cancer
risk (CR = 1 x 10-3) exists if groundwater contaminated with
vinyl chloride was consumed over a long exposure period by
the resident(s) drinking from a contaminated well. The
final scenario which was evaluated in the BLRA was use of
the landfill itself for residential structures. Under this
scenario, an unacceptable cancer risk (CR = 5 x 10-3) and
non-cancer risk (HI = 100) is posed by using the leachate as
a groundwater source, inhalation of volatile organic
compounds, surface soil exposure and consumption of home
grown vegetables.
ENVIRONMENTAL RISKS
The purpose of the ecological assessment is to identify
contaminants of potential ecological concern associated with
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SCALE IN FEET
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1000
FIGURE 5
ECOLOGICAL FEATURES
WOODSTOCK MUNICIPAL LANDFILL
WOODSTOCK. IL
-------
10
the site and their effects on plant or animal species of
concern. The ecological features of the site are shown on
Figure 5. The assessment conducted for the Woodstock site
has determined that copper, mercury, and zinc concentrations
in the surface soils at the site may adversely affect small
terrestrial mammal populations. Exposure of aquatic species
to iron which was detected in exceedance of regulatory
criteria also poses a potential risk. No conclusions could
be reached as to whether past ecological effects have
occurred due to the presence of other inorganic contaminants
in surface water and sediments at the site due to the lack
of biota sampling or biological assays. Additional
ecological assessments will be conducted by the Natural
Resources Trustee/U.S. Fish and Wildlife Service at the
site.
SUMMARY
Actual and threatened releases of hazardous substances are
occurring from this site. The source of the risks originate
from the contaminants within and emanating from the landfill
through releases to groundwater, surface water, sediments,
soils, and air. If not addressed, these releases may present
an imminent and substantial endangerment to public health,
welfare or the environment. Thus, it is necessary that
corrective and mitigative action be taken to address the
threats posed by the actual or threatened releases.
VII. DescriDtion of Alternatives
Based on the results of the RI, a list of alternatives was
assembled to address the site remedial action objectives and
ensure compliance with the requirements of the NCP. These
alternatives are presented in the Feasibility Study prepared
for the site. The following remedial alternatives were
developed and are briefly described below.
ALTERNATIVE 1
NO ACTION
CERCLA requires that the "No Action" alternative be
evaluated at every site to establish a baseline against
which all other alternatives are compared. Under this
alternative, no remedial actions would take place and the
site would remain in its present condition.
Capital cost: 0
Annual maintenance and monitoring cost:
Estimated present net worth: $37,000
Estimated time to implement: None
$10,000
-------
11
Note: The $10,000 maintenance and monitoring cost is not an
annual cost, but reflects the cost of reviewing site
conditions on a five year basis.
ALTERNATIVE 2 ACCESS RESTRICTIONS, INSTITUTIONAL
CONTROLS AND MONITORING
The purpose of Alternative 2 is to control access to the
site, and to monitor the groundwater and existing landfill
cover. The major elements of this alternative include:
*
*
Institutional controls
Fencing
Monitoring
*
Institutional controls would include land use restriction
and deed restrictions to preclude groundwater usage.
A chain-link fence would be installed and maintained around
the perimeter of the site. The purpose of the fence would
be to control access to the site, and thus, limit exposure
to the surface soils on-site. Erosion control measures
would be taken during fence construction to protect the
adjacent wetlands.
The primary objectives of monitoring would be to monitor
groundwater quality, wetlands water quality, and the
condition of the existing landfill cover. Groundwater
sampling and analysis would be conducted on a periodic
basis. Visual inspections of the cover and monitoring for
differential settlement would also be performed. The
frequency of all sampling activities or inspections will be
determined by the USEPA and IEPA (the "Agencies") during
Remedial Design.
Capital cost: $124,000
Annual maintenance and monitoring cost:
Estimated present net worth: $614,000
Estimated time to implement: 1 month
$25,000
ALTERNATIVE 3 - ACCESS RESTRICTIONS, INSTITUTIONAL CONTROLS,
GROUNDWATER EXTRACTION SYSTEM, AND MONITORING
The purpose of Alternative 3 is to control access to the
site, contain and treat the contaminated groundwater, and
monitor the groundwater and existing landfill cover. The
major elements of this alternative are:
*
*
Institutional controls
Fencing
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12
*
*
Monitoring
Groundwater extraction, treatment, and discharge
Institutional controls would include land use restrictions
and deed restrictions to preclude groundwater usage.
A chain-link fence would be installed and maintained around
the perimeter of the site. The purpose of the fence would
be to control access to the site, and thus, limit exposure
to the surface soils on-site. Erosion control measures
would be taken during fence construction to protect the
adjacent wetlands.
The objectives of monitoring would be to assess the
following: treatment system efficiency, groundwater and
wetland quality, and the condition of the existing landfill
cover. Groundwater and treatment system sampling and
analyses would be conducted on a periodic basis. The
landfill cover would also be periodically inspected visually
and monitored for differential settlement. The frequency of
all sampling activities and inspections will be determined
by the Agencies during Remedial Design. .
The groundwater extraction system would consist of
installing groundwater extraction wells in the area of vinyl
chloride contamination. Groundwater would then be pumped
from the extraction system to the publicly owned treatment
works (POTW). On-site treatment will be required only if
pretreatment standards are exceeded during this action.
Capital cost: $576,000
Annual maintenance and monitoring cost: $101,000
Estimated present net worth: $1,414,000
Estimated time to implement: 6 months
ALTERNATIVE 4 - INSTITUTIONAL CONTROLS, RECONSTRUCT EXISTING
COVER, AND MONITORING
The purpose of Alternative 4 is to minimize infiltration,
promote surface water runoff, eliminate leachate seeps, and
isolate the contaminants of concern. The major elements of
this alternative include:
*
*
Institutional controls
Monitoring
Cover reconstruction
*
Institutional controls would include land use restrictions
and deed restrictions to preclude groundwater usage.
Periodic monitoring would be conducted to evaluate the
-------
13
condition of the reconstructed landfill cover, the
sedimentation basin and wetlands water quality, and
groundwater quality. The reconstructed cover would
monitored periodically for differential settlement.
frequency of all sampling activities and inspections
determined by the Agencies during Remedial Design.
be
The
will be
The landfill cover would be reconstructed by removing
existing trees and brush on the landfill, sealing leachate
seeps, regrading the site, locating a suitable borrow site
for fill material, importing fill material as necessary,
placing this fill on top of the existing surfac~ soils, and
vegetating the new cover. A minimum cover thickness of 2
ft. would be established over the entire landfill. In areas
where sewage s:udge has been deposited on the landfill, a
minimum of 6 i~. of new soil will be placed, regardless of
the depth of existing cover soils. Th~ reconstructed cover
would also be sloped by filling and regrading to promote
surface water drainage from the landfill area. The
reconstructed cover would extend to the edge of the landfill
and would avoid the adjacent wetlands. The trees and brush
removed from the landfill would be appropriately disposed
of, as approved by the Agencies. Erosion control measures
would be taken to protect the perimeter wetlands. A surface
water control system would also be part of this remedy.
Capital cost: $4,418,000
Annual maintenance and monitoring cost: $69,000
Estimated present net worth: $5,770,000
Estimated time to implement: 6 months
ALTERNATIVE 5 - INSTITUTIONAL CONTROLS, RECONSTRUCT EXISTING
COVER, GROUNDWATER EXTRACTION SYSTEM, AND MONITORING
The major elements of Alternative 5 are the same as
Alternative 4 with remediation of contaminated groundwater
included. These elements would therefore include:
*
*
Institutional controls
Monitoring
Cover reconstruction
Groundwater extraction,
treatment, and discharge
*
*
The first three elements of this alternative were discussed
in Alternative 4. The fourth element, the groundwater
extraction system, would consist of installing groundwater
extraction wells in the area of vinyl chloride
contamination. Groundwater would then be pumped from the
extraction system to an on-site treatment facility if the
POTW pretreatment standards were exceeded during this
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14
action.
Capital cost: $4,860,000
Annual maintenance and monitoring cost: $129,000
Estimated present net worth: $6,490,000
Estimated time to implement: 6 months
ALTERNATIVE 6 - INSTITUTIONAL CONTROLS, CONSTRUCT
GEOSYNTHETIC CLAY CAP, AND MONITORING
The purpose of Alternative 6 is to minimize infiltration,
promote surface water runoff, eliminate leachate seeps, and
isolate the contaminants of concern. The major elements of
this alternative include:
*
*
Institutional controls
Monitoring
Geosynthetic clay cap
*
Institutional controls would include land use restrictions
and deed restrictions to preclude groundwater usage.
The primary objectives of monitoring would be to monitor
sedimentation basin and wetlands water quality, groundwater
quality, and the condition of the landfill cap. Periodic
groundwater sampling and analysis would be performed.
Regular visual inspections would be conducted to evaluate
the integrity of the landfill cap, and to check for erosion
and differential settlement.
The landfill cap would be constructed as specified in 35 IAC
811.314. Generally, this includes removing the existing
trees and brush, regrading the surface, sealing the leachate
seeps, placement of a geosynthetic liner with a bentonite
component, placement of a drainage layer, a rooting zone
layer, and topsoil. The cap would then be revegetated.
The geosynthetic clay layer would have a permeability
comparable to 3 ft. of compacted clay (1 x 10~ cm/s). The
geosynthetic clay cap would extend to the edge of the
landfill and would avoid the adjacent wetlands. The trees
and brush removed from the landfill would be appropriately
disposed of, as approved by the Agencies. The drainage
layer will be designed so as to route landfill gases to a
venting system. Erosion control measures would be taken to
protect the perimeter wetlands. A surface water control
system will be designed appropriate to the final grade such
that it will limit erosion of the landfill cover from sheet
flow, will not cause degradation of adjacent wetlands, meet
local stormwater retention requirements, and allow for the
monitoring of surface water runoff at distinct discharge
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15
points.
Capital cost: $6,612,000
Annual maintenance and monitoring cost: $69,000
Estimated present net worth: $7,964,000
Estimated time to implement: 6 months
ALTERNATIVE 7 - INSTITUTIONAL CONTROLS, CONSTRUCT
GEOSYNTHETIC CLAY CAP, GROUNDWATER EXTRACTION SYSTEM, AND
MONITORING
The major elements of Alternative 7 are the same as those in
Alternative 6 with remediation of contaminated groundwater
included. These elements would therefore include:
*
*
Institutional controls
Monitoring
Geosynthetic clay cap
Groundwater extraction,
treatment, and discharge
*
*
The first three elements of this alternative were discussed
in Alternative 6. The fourth element, the groundwater
extraction system, would consist of installing groundwater
extraction wells in the area of vinyl chloride
contamination. Groundwater would then be pumped from the
extraction system to the POTW. On-site treatment will be
required only if pretreatment standards are exceeded during
this action.
Capital cost: $7,054,000
Annual maintenance and monitoring cost: $129,000
Estimated present net worth: $8,681,000
Estimated time to implement: 6 months
ALTERNATIVE 8 - INSTITUTIONAL CONTROLS, CONSTRUCT RCRA
SUBTITLE D (i.e., SOLID WASTE-TYPE) CAP, AND MONITORING
The purpose of Alternative 8 is to minimize infiltration,
promote surface water runoff, eliminate leachate seeps, and
isolate the contaminants of concern. The major elements of
this remedy include:
*
*
Institutional controls
Monitoring
Solid waste-type cap
*
Institutional controls would include land use restrictions
and deed restrictions to preclude groundwater usage.
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16
The primary objectives of monitoring would be to monitor
sedimentation basin and wetlands water quality, groundwater
quality, and the condition of the landfill cap. Periodic
groundwater sampling and analysis would be performed.
Regular visual inspections would be conducted to evaluate
the integrity of the landfill cap, and check for erosion and
differential settlement.
Cap construction would involve the construction of a RCRA
Subtitle D solid waste-type cap which would seal the
leachate seeps, limit infiltration, and promote surface
water drainage from the landfill area. Construction would
begin with removal of the trees and brush on the landfill.
The trees and brush removed would be appropriately disposed
of, as approved by the Agencies. A borrow site would be
located for fill materials, of which a clay source will be
of primary importance. Fill material would be imported to
provide grades suitable for positive drainage. The
constructed cap would generally consist of a low
permeability clay layer placed to a compacted thickness of 3
ft. A 2.5 ft. protective soil cover may be placed above the
clay. A 6 in. organic topsoil layer may then be placed and
vegetated.
Capital cost: $9,204,000
Annual maintenance and monitoring cost: $69,000
Estimated present net worth: $9,854,000
Estimated time to implement: 9 months
ALTERNATIVE 9 - INSTITUTIONAL CONTROLS, CONSTRUCT RCRA
SUBTITLE D (i.e., SOLID WASTE-TYPE) CAP, GROUNDWATER
EXTRACTION SYSTEM, AND MONITORING
The major elements of Alternative 9 are the same as
Alternative 8 with remediation of contaminated groundwater
included. These elements would therefore include:
*
*
Institutional controls
Monitoring
Solid waste-type cap
Groundwater extraction,
treatment, and discharge
*
*
The first three elements of this alternative were discussed
in Alternative 8. The fourth element, the groundwater
extraction system, would consist of installing groundwater
extraction wells in the area of vinyl chloride
contamination. Groundwater would then be pumped from the
extraction system to the POTW. On-site treatment will be
required only if pretreatment standards are exceeded during
this action.
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17
Capital cost: $9,646,000
Annual maintenance and monitoring cost: $129,000
Estimated present net worth: $11,273,000
Estimated time to implement: 9 months
ALTERNATIVE 10 - INSTITUTIONAL CONTROLS, CONSTRUCT RCRA
SUBTITLE C (i.e., HAZARDOUS WASTE-TYPE) CAP, AND MONITORING
The purpose of Alternative 10 is to minimize infiltration,
promote surface water runoff, eliminate leachate seeps and
isolate the contaminants of concern. The major elements of
this remedy include:
*
*
Institutional controls
Monitoring
Hazardous waste-type cap
*
Institutional controls would include land use restrictions
and deed restrictions to preclude groundwater usage.
The primary objectives of monitoring would be to monitor
sedimentation basin and wetlands water quality, groundwater
quality, and the condition of the landfill cap. Groundwater
sampling and analysis would be done on a periodic basis.
Periodic visual inspection of the landfill cap and
monitoring for differential settlement would also be
performed.
Cap construction would involve the construction of a RCRA
Subtitle C hazardous waste-type cap which would seal the
leachate seeps, limit infiltration, and promote surface
water drainage from the landfill area. Construction of the
landfill cap would begin with removal of the trees and brush
on the landfill. The trees and brush removed would be
appropriately disposed of, as approved by the Agencies. A
borrow site would be located for fill materials, of which a
clay source will be of primary importance. Fill material
would be imported to provide grades suitable for positive
drainage. The RCRA Subtitle C cap would generally include
the following components: a 2 ft. thick compacted clay
layer, a 40 mI. high density polyethylene flexible membrane
liner, a 1 ft. thick drainage layer, an 18 in. rooting zone,
a 6 in. topsoil layer, and a vegetative cover.
Capital cost: $12,244,000
Annual maintenance and monitoring cost:
Estimated net worth: $13,596,000
Estimated time to implement: 1 year
$69,000
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18
ALTERNATIVE 11 - INSTITUTIONAL CONTROLS, CONSTRUCT RCRA
SUBTITLE C (i.e., HAZARDOUS WASTE-TYPE) CAP, GROUNDWATER
EXTRACTION SYSTEM, AND MONITORING
The major elements of Alternative 11 are the same as
Alternative 10 with remediation of contaminated groundwater
included. These elements would therefore include:
*
*
Institutional controls
Monitoring
Hazardous waste-type cap
Groundwater extraction, treatment
and discharge
*
*
The first three elements of this alternative were discussed
in Alternative 10. The fourth element, the groundwater
extraction system, would consist of installing groundwater
extraction wells in the area of vinyl chloride
contamination. Groundwater would then be pumped from the
extraction system to the POTW. On-site treatment would be
required only if pretreatment standards were exceeded during
this action.
Capital cost: $12,686,000
Annual maintenance and monitoring cost: $129,000
Estimated present net worth: $14,313,000
Estimated time to implement: 1 year
VIII. Evaluation of Alternatives
The NCP requires that the alternatives be evaluated against
nine evaluation criteria. This section summarizes the
relative performance of the alternatives by highlighting the
key differences among the alternatives in relation to these
criteria. The nine evaluation criteria are categorized as:
(1) Threshold Criteria; (2) Primary Balancing Criteria; and
(3) Modifying Criteria. Each of these terms is described as
follows:
o
Threshold Criteria
1) OVerall protection of human health and.the
environment addresses whether a remedy
provides adequate protection of human health
and the environment and describes how risks
posed through each exposure pathway are
eliminated, reduced or controlled through
treatment and engineering controls. The
selected remedy must meet this criteria.
2) Compliance with applicable or relevant and
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19
appropriate requirements (ARARs) addresses
whether a remedy will meet federal and state
environmental laws or justifies a waiver from
such requirements. The selected remedy must
meet this criteria or waiver of the ARAR must
be obtained.
o
Primary Balancinq Criteria
3) Long-term effectiveness and permanence
refers to expected residual risk and the
ability of a remedy to maintain reliable
protection of human health and the
environment over time, once cleanup goals
have been met.
4) Reduction of toxicity, mobility, and
volume through treatment is the anticipated
performance of the treatment technologies a
remedy may employ.
5) Short-term effectiveness addresses the
period of time needed to achieve protection
and any adverse impacts on human health and
the environment that may be posed, until
cleanup goals are achieved.
6) Implementability is the technical and
administrative feasibility of a remedy,
including the availability of materials and
services needed to implement a particular
option.
7) Cost includes estimated capital and
operation and maintenance (O&M) costs, also
expressed as net present-worth cost.
o
Modifvinq Criteria
8) Support Agency (IEPA) acceptance reflects
aspects of the preferred alternative and
other alternatives the IEPA favor or object
to, and any specific comments regarding
federal and state ARARs or the proposed use
of waivers.
9) Community acceptance summarizes the
pUblic's general response to the alternatives
described in the proposed plan and in the
RIfFS, based on public comments received.
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20
A detailed discussion of all the alternatives, including the
"No Action" alternative, has been provided in the FS. This
evaluation also includes an evaluation against the nine
criteria. The NCP requires that the "No Action" alternative
be evaluated to establish a baseline against which all other
alternatives are measured. A summary of the evaluation
discussion is provided below.
Overall Protection of Human Health and the Environment
Based upon the detailed analysis, it was concluded that
Alternatives 1 through 5 would not satisfy the criterion of
ensuring the overall protection of human health and the
environment. The baseline risk assessment has documented
unacceptable risks present at the site and these
alternatives do not meet the criterion either because no
remedial action would be taken (Alternative 1) or the
remedial actions specified would not adequately address the
present and future risks posed by the site, or adequately
prevent further leachate generation and releases of
contaminants to the environment.
The remaining Alternatives, 6 through 11, would be
protective of human health and the environment in regards to
exposure to surface soils. The differences in cap design
among these alternatives is a function of their complexity
and would not result in increased protectiveness from
surface soil exposure. However, the increased cap
complexity would affect leachate generation with the cap
specified in Alternatives 10 and 11 yielding the least
amount of leachate generation. The surface water seeps
which are a result of leachate generation are expected to be
eliminated through placement of a cap on the landfill. The
caps for Alternatives 6 through 9 would permit slightly
greater infiltration rates than the caps for Alternatives 10
and 11. This would result in slightly greater leachate
generation than that provided by Alternatives 10 a~d 11.
The caps proposed may have the undesirable effect of
trapping gas inside the landfill, resulting in a potential
increase in lateral migration of landfill gas. This will be
remedied through placement of a venting system in the
landfill.
Alternatives 6, 8, and 10 would not be protective of human
health and the environment with respect to groundwater in
that no remedial activities are proposed in these .
alternatives to address this potential or actual risk to
human health and the environment.
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21
Compliance With ARARS
Only Alternative 7 would comply with all chemical, action,
and location specific ARARs associated with the site. More
specifically, Alternatives 1 through 5 would not comply with
the action-specific or chemical-specific ARARs which require
landfill capping (IAC 811) and remediation of the
contaminated groundwater (40 CFR 141 and 35 IAC 620.410) .
Alternatives 6, 8, and 10 would not comply with chemical-
specific ARARs since these alternatives do not require
remediation of the contaminated groundwater. Alternatives 9
and 11 would not meet the location-specific ARAR (40CFR 6)
since these alternatives would result in the 10S5 of
wetlands due to cap placement and other remedial
alternatives exist which would not require mitigating the
loss of these wetlands. If an alternative were chosen that
results in a loss of wetlands, mitigating the loss of those
wetlands generally requires replacement on a 2 to 1 ratio.
A listing of all ARARs associated with each alternative can
be found in Table 11 of the FS.
Lonq-ter.m Effectiveness and Permanence
Capping the landfill would contain the surface soils,
sediments, sludges and wastes effectively. A cap would
permanently reduce infiltration into the landfill therefore
reducing leachate generation to the maximum extent
practicable. Alternatives 10 and 11 would provide the most
effective infiltration reduction option of all the
alternatives. However, since the waste mass is in contact
with groundwater, the more effective infiltration reduction
achieved by Alternatives 10 and 11 is not considered to be
significant in comparison to either of the caps specified in
Alternatives 6 and 7 or 8 and 9. All the capping
alternatives (4 through 11) would eliminate human exposure
to the contaminated surface soils and would' also minimize
the ecological risks posed by this media with Alternatives
10 and 11 being most protective due to the thickness of the
cap.
The alternatives addressing groundwater extraction (3, 5, 7,
9, and 11) would be effective in preventing further
migration of the vinyl chloride and would ultimately
eliminate the threat posed by this media through extraction
and treatment.
Reduction of Toxicitv. Mobility or Volume
None of the alternatives would reduce toxicity or volume of
the in-situ landfill wastes. Alternatives 1 through 3 would
only require monitoring and institutional controls.
Alternatives 4 through 11 are containment alternatives and
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22
would also not reduce the toxicity and volume of.in-situ
wastes. However, the capping alternatives would reduce the
volume of leachate being produced by minimizing
infiltration. This would also reduce the mobility of the
contaminants. Alternatives 5, 7, 9, and 11 would reduce the
toxicity, mobility and volume of contaminants in the
groundwater through an active groundwater extraction system.
Short-term Effectiveness
Alternatives 5, 7, 9, and 11 would result in compliance with
groundwater standards through extraction of the contaminated
groundwater and treatment at the POTW. A higher level of
risk is associated with these alternatives due to the
potential dewatering of the wetlands. Design of the system
must preclude this from occurring. In addition, erosion
controls, drainage swales, and sedimentation basins are
necessary to protect the wetlands during construction as
well as after construction is complete. Remediation
activities would also result in increased risk of injury due
to increased truck traffic on other related construction
activities. The increase in dust generation must also be
mir-~~ized through dust control measures or the use of
personal protective equipment by workers. It is expected
that the duration of capping activities specified in
Alternatives 4 through 11 will not exceed one year.
Remediation of the contaminated groundwater as called for in
Alternatives 3, 5, 7, 9, and 11 is not expected to exceed
five years.
Imp1ementabilitv
All the alternatives are readily implementable. The capping
alternatives and those alternatives specifying groundwater
extraction have been proven to be an effective technology in
remediating similar threats on other sites. Technologies
for constructing a groundwater extraction system are
relatively easy to implement, well developed, and are
reliable. If treatment is required before discharge, the
technologies for treatment are proven and readily
implementable.
Cost
The costs for the eleven identified alternatives range from
$37,000 (Alternative 1) up to $14,313,000 (Alternative 11)
in terms of-present net worth. The capital costs range from
$0 (Alternative 1) up to $12,686,000 (Alternative 11). The
following summary table lists each alternative and the
associated costs:
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23
ALTERNATIVE COSTS II
Capital 0&1>1 PNW
1. No Action $0 $10,000 $37,000 ,.
2 . Access Restrictions and
Monitoring $124,000 $25,000 $614,000
3. Access Restrictions,
Groundwater Extraction
System, and Monitoring $576,000 $101,000 $1,414,000
4. Access Restrictions,
Reconstruct Existing Cover,
and Monitoring $$3,935,000 $69,000 $$5,287,000
5. Access Restrictions,
Reconstruct Existing Cover,
Groundwater Extraction
System, and Monitoring $4,378,000 $129,000 $6,005,000
6. Access Restrictions,
Construct Geosynthetic Clay
Cover, and Monitoring $6,612,000 $69,000 $7,964,000
7. Access Restrictions,
Construct Geosynthetic Clay
Cover, Groundwater
Extraction System, and
Monitoring $7,054,000 $129,000 $8,681,000
8. Access Restrictions,
Construct RCRA Subtitle D
(Le., solid waste-type)
Cover, and Monitoring $9,204,000 $69,000 $9,854,000
9. Access Restrictions,
Construct RCRA Subtitle D
(Le., solid waste-type)
Cover, Groundwater
Extraction System, and '
Monitoring $9,646,000 $129,000 $11,273,000
10. Access Restrictions,
Construct RCRA Subtitle C
(Le., hazardous waste-type)
Cover, and Monitoring $12,244,000 $69,000 $13,596,000
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24
ALTERNATIVE COSTS
Capital O&M PNW
11. Access Restrictions,
Construct RCRA Subtitle C
(i.e., hazardous waste-type)
Cover, Groundwater
Extraction System, and
Monitoring $12,686,000 $129,000 $14,313,000
State Acceptance
The State of Illinois, through IEPA, is expected to concur
with the u.S. EPA's recommendation of Alternative 7 as the
preferred alternative for the Woodstock site.
Community Acceptance
A summary of both written and verbal comments received by
the U.S. EPA during the public comment period has been
attached as Appendix II. Generally, the remedy was highly
controversial due to the potential local tax implications
associated with implementing the remedy. As is reflected in
the attached summary, there was one faction of residents who
strongly supported the proposed remedy and another faction
in opposition.
IX.
Description of Selected Remedv
The U.S. EPA and IEPA have conducted an analysis of the
potential remedies and have selected Alternative 7 as the
remedy for the Woodstock site.
The purpose of Alternative 7 is to minimize infiltration,
promote surface water runoff, eliminate leachate seeps,
isolate the waste, and remediate the contaminated
groundwater. The major elements of this alternative
include:
*
*
Institutional controls
Monitoring
Geosynthetic clay cover
Groundwater extraction,
treatment, and discharge
*
*
Institutional controls will include land use restrictions to
prevent future development of the site and adjoining
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25
property and to preclude construction of any structure which
may be detrimental to the remedy. Deed restrictions are
already in place at the site which preclude groundwater
usage and would be amended and expanded, as necessary, to
the satisfaction of the Agencies to prohibit the
installation of water supply wells on property which could
potentially be impacted by vinyl chloride contamination.
The primary objectives of monitoring will be to monitor
sedimentation basin and wetlands water quality, groundwater
quality, and the condition of the landfill cover. Periodic
groundwater sampling and analysis will be perfopmed.
Regular visual inspections will be conducted to evaluate the
integrity of the landfill cover, and check for erosion and
differential settlement. Long term maintenance will be
conducted to assure that the components of this remedy
remain effective. The frequency of all sampling activities
and inspections will be determined by the Agencies during
Remedial Design.
The landfill cap would be constructed as specified in 35 IAC
811.314. Generally, this includes removing the existing
trees and brush on the landfill, placement of the
contaminated soils and sediments on the landfill surface,
regrading the surface using existing on-site soils and at
least 6 inches of supplemental granular soils to achieve and
maintain positive drainage, sealing the leachate seeps,
placement of a geosynthetic membrane which will include a
bentonite layer, placement of a drainage layer, a rooting
zone layer, and topsoil. The cap would then be revegetated.
During the design of the remedy, the potential use of native
vegetation will be investigated in conjunction with the Soil
Conservation Service. The final cap design and vegetative
cover will then be selected at the completion of this
process. The barrier layer will have a permeability equal
or superior to 3 feet of compacted clay at 1X10-7 cm/s. The
geosynthetic clay cap will extend to the edge of the
landfill and will avoid the adjacent wetlands. Trees and
brush removed from the landfill would be appropriately
disposed of. The grading layer will be designed so as to
route landfill gases to a venting system. Perimeter side
slopes are to be regraded to allow for no impact to the
wetlands and accommodate the design requirements of the
landfill cap. Erosion control measures would be taken to
protect the perimeter wetlands. A surface water control
system will be designed appropriate to the final grade such
that it will limit erosion of the landfill cover from sheet
flow, will not cause degradation of adjacent wetlands, meet
local stormwater retention requirements, and allow for the
monitoring of surface water runoff at distinct discharge
points. The precise design of the cap components and
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26
associated engineering or environmental requirements will be
reviewed and approved by the Agencies during Remedial
Design.
The groundwater extraction system will consist of installing
groundwater extraction wells in the area of vinyl chloride
contamination. Groundwater would be pumped from the
extraction system to an on-site treatment facility if the
POTW pretreatment standards were exceeded. The goal of this
remedial action is to restore ground water to its beneficial
use, which is, at this site, a drinking water resource.
Therefore, remediation will continue until such. time that
the MCL (and equivalent state standard) of 2 ppb is
attained. Based on information obtained during the remedial
investigation and on a careful analysis of all remedial
alternatives, u.s. EPA and IEPA believe that the selected
remedy will achieve this goal. However, it may become
apparent, during design, implementation or operation of the
ground water extraction system and its modifications, that
contaminant levels have ceased to decline and are remaining
constant at levels higher than the remediation goal over
some portion of the plume or that a more effective
technology may be warranted. In such a case, the system
performance standards and/or the remedy may be evaluated and
changes to the system or a different technology may be
required which would allow the Agencies to achieve ARARs.
The selected remedy will include ground water extraction
during which the system's performance will be carefully
monitored on a regular basis, as determined by the Agencies,
and adjusted as warranted by the performance data collected
during operation. Modifications may include any or all of
the following:
o
Discontinuing pumping at individual wells where cleanup
goals have been attained;
o
Alternating pumping at wells to eliminate stagnation
points;
o
Pulse pumping to allow aquifer equilibration and to
allow adsorbed contaminants to partition into ground
water;
o
Installing additional extraction wells to facilitate or
accelerate cleanup of the contaminant plume.
To ensure that cleanup levels are maintained and that the
cap prevents all further releases from occurring, the site
will be monitored on a frequency as required by the
Agencies. If further releases do occur, the Agencies may
require that further remedial actions are undertaken to
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27
eliminate these releases.
The sediments that contain levels of contamination that
exceed background levels will be excavated and placed under
the new landfill cover. The wetlands areas from which these
sediments are removed must then be restored to their
original conditions. Excavation and consolidation of these
sediments under the cap will reduce the exposure potential
to humans or wildlife to this contaminated media.
x.
Statutory Determinations
The selected remedy must satisfy the requirements of Section
121 of CERCLA to:
A.
B.
C.
D.
Protect human health and the environmentj
Comply with ARARsj
Be cost-effective;
Utilize permanent solutions and alternate
treatment technologies to the maximum extent
practicablej and
Satisfy the preference for treatment as a
principle element of the remedy.
E.
The implementation of the selected remedy at the Woodstock
site satisfies the requirements of CERCLA as detailed below:
A.
Protection of Human Health and the Environment
Implementation of the selected remedy will reduce and
control potential risks to human health posed by exposure to
contaminated ground water, soil, landfill waste, surface
water, and sediments. The selected remedy will reduce
potential exposure to contaminated groundwater and surface
soils to within acceptable an acceptable risk range. The
contaminated groundwater will be remediated until the MCL of
2 ppb is reached. The selected remedy also protects the
environment from the potential risks posed by contaminants
discharging to ground water, Kishwaukee River, surrounding
soils, sediments, and wetlands.
Institutional controls will be implemented to protect
against drinking of contaminated ground water at the site'
and prohibit construction which could be detrimental to the
remedy.
Capping the landfill, in addition to reducing the potential
risk posed by exposure to landfill contaminants, will reduce
precipitation infiltration through the cap thereby reducing
leachate generation. Ground water contaminant loading,
leachate generation, and seepage into the wetlands would
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28
then be reduced or eliminated.
Gas venting will reduce potential risks due to the landfill
gases.
Excavation and consolidation of contaminated sediments under
the landfill cap will reduce the exposure potential to
humans or wildlife posed by these sediments.
No unacceptable short-term risks will be caused by
implementation of the remedy. However, the nearby
community, and site workers, may be exposed to noise and
dust nuisances during construction. Standard safety
measures should manage any short-term risks. Dust control
measures would mitigate risks as well. Mitigative measures,
as specified during design, will be taken to prevent and
address adverse environmental impacts.
B.
ComDliance with ARARs
With respect to any hazardous substances, pollutants or
contaminants that will remain on-site, CERCLA (~ 121 (2)
(A)) requires the U.S. EPA to select a remedial action which
complies with legally applicable or relevant and appropriate
standards, requirements, criteria or limitations (ARARs).
The selected remedy will comply with Federal ARARs or State
ARARs where State ARARs are more stringent, as determined by
U.S. EPA. The remedy will be implemented in compliance with
applicable provisions of CERCLA and the NCP.
1.
Chemical-Specific ARARs
Chemical-specific ARARs regulate the release to the
environment of specific substances having certain chemical
characteristics. Chemical-specific ARARs typically define
the extent of cleanup at a site.
a.
Soils/Sediments
There are no chemical-specific standards established for
soils and sediments.
b.
Ground Water
i) .
Federal ARARs
Maximum Contaminant Levels (MCLs), Maximum Contaminant Level
Goals (MCLGs), and Secondary Maximum Contaminant Levels
(SMCLs) are ARARs for the site.
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29
ii). State ARARs
The State of Illinois is authorized to administer the
implementation of the Federal SDWA. The State also has
ground water quality standards promulgated under Title 35,
Subtitle F, Chapter I, Part 620. According to the State of
Illinois' classification system, the aquifer underlying the
site is Class I potable resource groundwater. Class I
groundwqter quality standards listed under 620.410 are ARARs
for the ground water at the Woodstock site.
In the event that discharge of the contaminated groundwater
to the POTW is not acceptable without on-site treatment, IAC
35, Part 218 would then be an ARAR for the site.
c.
Surface Water
i) .
Federal ARARs
Federal water quality criteria (WQC) are guidelines that set
pollutant concentration limits to protect surface waters
that are applicable to point source discharges, such as from
industrial or municipal wastewater streams. At a Superfund
site, the Federal WQC would not be ARARs except for
pretreatment requirements for discharge of treated water to
a Publicly Operated Treatment Works (POTW). Since the
selected remedy plans to discharge to the local POTW, these
requirements are ARARs for the Woodstock site. The AWQCs
for protection of freshwater aquatic organisms are ARARs for
the Woodstock site remedy for any direct discharges to the
Kishwaukee River. .
ii). State ARARs
The State of Illinois has been authorized to implement the
National Pollutant Discharge Elimination System (NPDES)
established under the CWA, as specified in IAC 35, Part 309.
For any discharge to waters of the State of Illinois, the
chemical specific standards of Title 35, Subtitle C, Subpart
B, Section 302.208 and toxic substances standards of Section
302.210 of the Illinois Administrative Code establishing
General Use Wa~er Quality Standards would be ARARs.
2.
Location Specific ARARs
Location-specific ARARs are those requirements that relate
to the geographical position of a site. These include:
a.
Federal ARARs
40 CFR 6 - Protection of Wetlands is an ARAR for any
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30
remedial action taken within wetlands. This ARAR requires
that activities required in a wetland must minimize the
destruction, loss, or degradation of the wetland. In
addition, any affected wetlands may be restored, as
appropriate. In addition, a permit from the U.S. Army Corps
of Engineers may be required due to the potential that
activities during construction may impact the wetlands.
Endangered Species Act (16 USC 1531) - The Endangered
Species Act requires that actions must be performed to
conserve the endangered or threatened species located in and
around the Woodstock site. Activities must not destroy or
adversely modify the critical habitat upon which endangered
species depend. The selected remedy will be implemented in
compliance with this regulation.
b.
State ARARs
Endangered Species Protection Act, Title 17 Conservative
Chapter 1, Subchapter C, Part 1075 Illinois Administrative
Rules - Under this requirement, actions must be performed to
conserve the endangered or threatened species located in and
around the Woodstock site. Activities must not destroy or
adversely modify the critical habitat upon which endangered
species depend. The selected remedy will be implemented in
compliance with this regulation. Prior to conducting
remedial activities, a s~rvey of the subject areas will be
conducted to determine whether or not endangered or
threatened species will be affected.
3 .
Action-Specific ARARs
Action-specific ARARs are requirements that define
acceptable treatment and disposal procedures for hazardous
substances.
It is unknown at this time whether or not the collected
ground water will require treatment prior to discharge to
the POTW. If required, any treatment system utilized will
be operated in compliance with all ARARs including 40 CFR
403.
40 CFR 122 is an ARAR at this site in regards to surface
water runoff which includes stormwater runoff.
29 CFR 1910 and 1926 are OSHA requirements which are ARARs
at the site.
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31
a.
State ARARs
The selected remedy will comply with substantive
requirements of Title 35, Illinois Solid and Special Waste
Management Regulations, Section 811, Subpart C for closure
of solid wastes landfills, specifically relating to final
cover, air pollution, and closure requirements, as required.
Groundwater that is treated and discharged shall comply with
35 lAC, Part 307 as well as 35 lAC, Part 310 which are ARARs
for this site since pretreatment standards, permitting, and
reporting requirements must be met for POTW discharge.
35 lAC, Part 620.250 which provides for the establishment of
a groundwater management zone is an ARAR for the site.
C.
Cost Effectiveness
Cost effectiveness is determined by evaluating the following
three of the five balancing criteria to determine overall
effectiveness: long-term effect~veness and permanence,
reduction of toxicity, mobility or volume through treatment,
and short-term effectiveness. Overall effectiveness is then
compared to cost to ensure that the remedy is cost
effective.
The selected remedy provides overall cost effectiveness
because it provides adequate long-term effectiveness and
permanence. Secondary reduction in toxicity, mobility, and
volume is accomplished through treatment of the ground
water. No unacceptable short-term risks will be caused by
implementation of the remedy.
D.
Utilization of Permanent Solutions and Alternative
Treatment Technologies or Resource Recovery
Technoloqies to the Maximum Extent Practicable
The selected remedy utilizes permanent solutions and
alternative treatment technologies to the maximum extent
practicable. This finding was made after evaluation of the
protective and ARAR-compliant alternatives for the Woodstock
site remedial action and comparison of the "trade-offs"
(advantage vs. disadvantages) among the remedial
alternatives with respect to the five balancing criteria
(see discussion above) .
E.
Preference for Treatment as a Principle Element
The principle threats at the Woodstock site are the
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32
contaminated ground water and contaminated soil and
leachate. The selected remedy uses treatment as a secondary
element of the remedy through the collection and treatment
of contaminated groundwater. Due to the large volume and
heterogeneous distribution of waste throughout the landfill,
treatment of the landfill material itself is not practicable
at this site.
-------
APPENDIX III
DATA TABLES
.
-------
MONITORING WELLS
.
-------
, ,t
ANALYTICAL DATA REPORT
Uoodstock lendflll RI/FS
Uoodstock, Illinois
Hatrlx: CU Type: IND HIl
Cenerated by: CAU
Dete Issued: 10-HAY-91
Parameter WK-GY8BOI-01 11/02/90 UK.CUSB02-02 02/06/91 UK-CUFBOI-01 10/31/90 UK-CUFB02.01 11/02/90 UK-~F806-02 02/07/91
-.-.....----------...-.-...----- .....-....-.......------ ------------------------ .-.-...----......--.-.---..-- --- --....-------..... ---...... -- -.--.........- ---..... -.... --.. ---
Alunlnun (UC/l) 200. U/ 67. K/ 200. UI 200. U/ 50. U/
Ant lmony (UC/l) 50. U/ 5. UN/ 50. II/ 50. U/ 5. UNS/
Arsenic (IIC/l) 2. II/ 2. U/ 2. II/ 2. U/ 2. U/
Bar hlft (UC/l) 10. U/ 10. UI 10. UI 10. U/ 10. U/
Beryillun (IIC/l) 0.2 U/ 5. U/ 0.2 II/ 0.2 U/ 5. tJ/
Cadnlun (IIC/U 5. U/ 5. UI 5. I 5. II/ 5. U/
Calclun (UC/l) 1000. U/ 1000. U/ 1000. U/ 1000. U/ 1000. U/
ChrOllllun, toUI (UC/l) 10. U/ 10. U/ 10. U/ 10. U/ 10. U/
Cobalt (UG/l) 50. U/ 10. UI 50. U/ 50. U/ 10. U/
Copper (UC/l) 11.. K/U 10. U/ 10. U/ 16. K/U 10. U/
Iron (UC/U 38. KI 14. 1(/ 20. U/ 20. U/ 20. U/
leed (UC/l) 3. U/ 3. US/ 3. U/ 3. II/ J. U/
Haunes lun (UC/l) 1000. U/ 1000. . U/ 1000. U/ 1000. II/ 1000. II/
Manganele (UC/l) 10. U/ 15. UI 10. U/ 10. III 15. U/
Hercury (UC/l) 0.2 U/ 0.2 UI 0.2 U/ 0.2 U/ 0.2 U/
Nickel (UC/l) 20. UI 20. U/ 20. U/ 20. U/ 20. UI
POUSS lun (UG/l) 100. U/ 100. U/ 100. U/ 100. U/ 110. K/
Selenlun (UG/l) 2. U/ 2. UI 2. UI 2. II/ 2. US/
Sliver (UC/U 10. UN/R 10. U/ 10. UN/R 10. UN/R 10. U/
Sodlu. (UC/l) 2000. U/ 1000. UN/ 2000. U/ 2000. U/ 1000. UNI
The I tfun (UC/l) 3. UI 3. U/ 3. U/ 3. U/ 3. U/
Venedlun (UG/l) 2. UI 50. U/ 2. U/ 2. U/ 50. U/
Zinc (IIC/l) 10. U/ 10. U/ 10. U/ 10. U/ 10. U/
Cyanide (UG/l) 10. U/ 10. U/ 10. U/ 10. U/ 10. U/
Alkalinity, Total (HG/l) 5. UI 5. U/ 5. U/ 5. II/ 5. U/
Chloride (HG/l) 1. U/ 1. U/ 1. U/ L II/ 1. U./UJ
Chemical OKygen Demand (HC/l) 20. U/ 21. /U
NltratetNltrlte Nitrogen (HG/l) 0.02 UI 0.01 / 0.02 U/ 0.02 UI 0.04 /
Nitrogen, Ammonia (HG/l) 0.1 U/ 0.1 U/ 0.1 U/ 0.1 II/ 0.1 U/
Nitrogen, Total Kjeldahl (HG/l) 0.1 /U 0.1 UN/UJ 0.1 U/ 0.29 / 0.1 UN/UJ
Phosphorus, Total (HG/l) 0.02 UN/ 0.02 UN/UJ 0.02 UN/ 0.02 UN/ 0.02 UN/UJ
Sui fete (HG/l) 5. UI 5. UI 5. U/ 5. U/ 5. UI
Total Dissolved Solids (HG/l) 20. U/ 20. U/ 20. UI 20. II/ 20. II/
Note: (1) Results /Ire reported with qualifiers (Ioboratory Qualifier/Data Validation Qualifier) to the right of the vAlue.
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ANALYTICAL DATA REPORT 2
Uoodstock landfill RllfS
Uoodstock, Illinois
Matrix: CII Type: IND Hfl
Par 811M! ter \lK-GUFBI0-02 04/02/91 \IK.GUMUOID.OI 10/31/90 \IK-CUMUOID-02 02/06/91 \IK-CUMUOIS-01 10/31/90 UK-CUMUOIS-02 02/06191
................----..---------- ------------------------ ------------------------ .......- --- --.. -- .....- --......... -- -....---------........ -.. -......_- ---------------..-..-..-..--
Ahnlnun (UG/l) 50. UI 200. UI 52. IC/U 200. UI 50. ul
Antimony (UG/l) 50. III 50. UI 5. UNI 50. UI 5. UNI
Arsenic (UG/l) 2. UI 2. UI 2. UI 5.9 ICSI 6. ICI
Berlun (UG/l) '0. UI 171. ICI 200. I 218. I 250. I
Beryiliun (UG/l) 5. UI 0.2 UI 5. UI 0.2 UI 5. UI
Cadlliun (UG/l) 5. UI 5. UI 5. UI 5. UI 5. UI
Calc:lun (UG/l) 1000. UI 126000. I 125000. I 9]500. I 83700. I
Chromlun, tote I (UG/l) 10. UI 10. UI 10. UI 10. UI 10. UI
Cobalt (UG/l) 10. UI 50. UI 10. UI 50. UI 12. IC/U
Copper (UG/l) 10. UI 10. UI 10. UI 10. UI 10. UI
I ran (UG/l) 20. UI 2370. I 1180. I 1340. I ]160. I
lead (UG/l) 3. UI 3. UI 3. UI ]. UI 3. UI
Hagnellun (UG/l) 1000. UI 56000. I 58400. I 77300- I 77200. I
Manganese (UG/l) 10. UI 163. I 174. I 553. I 827. I
Mercury (UG/l) 0.2 UI 0.2 UI 0.2 UI 0.2 UI 0.2 UI
Nickel (UG/l) 20. UI 20. UI 20. UI 77. I 9]. I
Potllliun (UG/l) 100. UI 11100. KI 2440. ICI 13200. I 15000. ICI
Selenlun (UG/l) 2. UI 2. UI 2. USI 2. UI 2. UI
Sliver WG/L> 10. UI 10. UN/R 10. UI 10. UN/R 10. UI
Sodlun (UG/l) 2000. UI 44000. / 67300. N/J 65000. I 58900. N/J
Thailiun (UG/l) 3. UI 3. UI 3. UI ]. UI 3. UI
Van8dlun (UG/l) 50- UI 2. UI 50. UI 2. UI 50. UI
Zinc (UG/l) 10. ul 10. UI 450. I 10. UI 49. I
CyanIde (UG/l) 10. UI 10. UI 10. UI 10. UI
Alklllnlty. Total (HC/l) 5. UI 3]6. I 359. I 668. I 622. I
Chtorlde (HG/l) 1. UI 142. I 198. I 36. I 29. I
Chemicil Oxygen Delllllnd (HG/L> 20. UI 52. IU
NltrltetNltrlte Nitrogen (HG/l) 0.02 UI 0.02 UI 0.02 UI 0.02 UI 0.02 UI
Nitrogen, Ammonia (HG/l) 0.14 N/J 0.32 I 0.52 I 5.62 I 8.65 I
Nitrogen, Total ICjeldahl (MG/l) 0.1 UI 0.19 IU 1.45 NIJ 5.~1 I 8.]4 N/J
Phosphorus, Total (HG/l) 0.02 UI 0.12 NI 1.]8 N/J t.09 N/J 1.08 N/J
SulfIte (HC/L> 5. UI 97. I 116. I 21. I 27. I
Total Dissolved Solids (HG/l) 24. I 696. I 794. I 756. I 704. I
Note: (1) Results are reported with quAlifiers (lAboratory Qual I fler/Data Validation Qualifier) to the right of the value.
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ANALYTICAL DATA REPORT ]
Uood5tock landfill RI/FS
Uoodstock. IIIInol5
Hatrlx: CU Type: IND HTl
Parameter UK-CUHU02D-01 10/31/90 UK-CUHU02D-02 02/06191 UK-CUHUD2S-01 10/]1/90 UK-CUHU02S-02 02/06/91 UK-CUHU02S'91 10/J1/90
-..a.............-.............. -...-.. --................ -- -------.... ...-- -"--------..- -----------------------... --.----------------..----- -------------..---------. ----..----..----......----......
Alunlnun (UC/l) 200. UI 50. UI 200. IU 50. UI 200. UI
AntImony WG/l) 50. UI 5. UNI 50. UI 5. UN I 50. III
Arsenic (IIC/l) 2. UI 2. UI 2.4 KI 3.8 kSI 2.7 kl
Berlun (UC/l) 138. KI 139. KI 308. I 247. I 344. I
Beryiliun (UC/l) 0.2 UI 5. UI 0.2 UI 5. UI 0.2 UI
Cachlun (UC/l) 5. UI 5. UI 5. UI 5. UI 5. UI
Caldun (UC/l) 97200. I 89200. I 154000. I 129000. I 171000. I
Chromlun. total (UG/l) 10. UI 10. UI 10. UI 10. UI 10. UI
Cabel t (UG/l) 50. UI 10. UI 50. UI 10. UI 50. UI
Copper (UG/l) 10. UI 10. UI 10. UI 10. UI 10. UI
Iron (IIC/l) 1180. I 1250. I 1070. I 1290. I 669. I
lead (UC/l) 3. UI 3. UI 3. UI 3. UI 3. UI
Hagneslun (UG/l) 54600. I 54400. I 77400. I 69000. I 85700. I
Hanganese (UG/l) 75. I 87. I 900. I 1090. I 909. I
Mercury (UG/l) 0.2 UI 0.2 UI 0.2 UI 0.2 UI 0.2 UI
Nickel (UC/l) 20. UI 20. UI 20. UI 20. UI 20. UI
Potasslun (UG/l) 1360. KI 1300. KI 8360. I 6290. I 9340- I
Selenlun (UC/l) 2. UI 2. UI 2. USI 2. UI 2. USI
Sliver (IIC/l) 10. UN/R 10. UI 10. UN/R 10. UI 10. UN/R
Sodlun (UC/l) 7760. I 9600. N/J 138000. I 125000. N/J 165000. I
Thai II un (UG/l) 3. UI 3. UI 3. UI 3. UI 3. U/'
Vanadlun (UC/l) 2. UI 50. UI 5.2 KI 50. UI 5.6 KI
Zinc (UC/l) 10. UI 12. KI 10. UI 222. I 10. UI
Cyanide (UG/l) 10. UI 10. UI 10. UI 10. UI 10. UI
Alkalinity. Total (HG/l) 413. I 416. I 606. I 644. I 657. I
Chloride (MG/L> 4. I 4. I 295. I 239. I 328. I
Ch~lcal Oxygen Demand (HG/l) 20. UI 42. IU
Nitrate-Nitrite Nitrogen (HC/l) 0.02 UI 0.02 UI 0.02 UI 0.02 UI 0.02 UI
Nitrogen. Ammonia (HG/l) 0.61 I 0.58 I 3.02 I ;;.06 I 2.53 I
Nitrogen. Total KJeldahl (HG/l) 0.68 I 0.62 NIJ 3.51 I 6.12 N/J 5. I
Phosphorus, Total (HG/l) 0.04 NI 0.15 NIJ 0.9 N/J 1. 75 N/J 1.79 N/J
Sulfate (HG/l) 83. I M. I 17. I 21. I 15. I
Total Dissolved Solids (HG/l) 512. I 498. I 1140. I 1010. I 1140. I
Note: (\) Results are reported with qualifiers (l.nbpratory Q"allfl~r/Data Validation QuaUfler) to the right o' the value.
-------
ANALYTICAL DATA REPORT 4
Uoodstock landfill RI/FS
Uoodstock, Illinois
Hatrix: GU Type: IND HTl
Parameter UK-GUHUOJD-OI 11/01/90 UK-GUHUOJD-02 02/06/91 UK-GUHUOJS.OI 11/01/90 UK-GUHUOJS.02 02/06/91 UK-GUHU04D-01 11/01/90
------ ..................... "'...-................. --.. ...........-........ ---....----........ ------.......-..-..--------..- ----........... --..........- -..-......... ...-----........--......... "'.._--"'.... ........ .... .... .. .... .... .................... ..
Alunlnun (IIC/l) 200. III 57. Kill 200. III 50. III 200. III
AntImony CUC/l) 50. III 5. IINI 50. UI 5. IINI 50. III
ArsenIc (IIG/l) 2. III 2. III 2. III 2. III 2. III
Barlun (IIG/l) 137. KI 138. KI 110. KI 83. KI 254. I
Beryiliun (IIC/l) 0.2 III 5. III 0.2 III 5. III 0.2 III
Cadnlun (IIG/l) 5. III 5. III 5. III 5. III 5. III
Calclun (IIG/l) 131000. I 124000. I 119000. I 106000. I 171000. I
Chromlun, totel (IIC/l) 10. III 10. III 10. III 10. UI 10. III
Cobal t (IIG/l) 50. III 10. UI 50. III 10. UI 50. III
Copper (UG/l) 10. III 10. III 10. III 10. III 10. III
Iron (UC/l) 101.0. I 1740. I 20. UI 20. III 1870. I
lead (IIC/l) 3. IISI 3. III 3. III 3. III 3. III
Magnealun (IIG/l) 63300. I M800. I 49200. I 1,7400. I 78300. I
Hanganese (IIC/l) 48. I 51,. I 1,51. I 310. I 529. I
Hercury (IIG/l) 0.2 III 0.2 III 0.2 III 0.2 III 0.2 III
N I ekel (IIC/l) 20. KI 20. III 27. KI 20. UI 20. III
Pot.aalun (IIC/l) 1240. KI 1150. KI 860. KI 510. Kill 2500. KI
Selenlun (IIC/l) 2. III 2. IISI 2. III 2. III 2. III
Sliver (IIG/l) 10. IIN/R 10. III 10. IIN/R 10. III 10. IIN/R
Sodlun (IIG/l) 7790. 1 81,00. N/J 18200. 1 17600. N/J 57700. I
Thall hm (IIC/l) 3. III 3. III 3. III 3. III 3. III
Vanadlun (IIG/l) 2. III 50. III 2. UI 50. III 2. UI
ZInc (IIG/l) 10. III 15. KI 10. III 52. I 10. III
CyanIde (IIC/l) 10. III 10. III 10. III 10. III 10. III
AlkalInIty, Total (HC/l) 438. I 494. I 1,28. I 417. 1 650. I
Chloride (HG/l) 1,. I 8. */J 15. I 25. */J 119. I
ChemIcal Oxygen Demand (HG/l) 20. III 20. III
Nltrate.Nitrite Nitrogen (HG/l) 0.02 III 0.02 III 0.02 III 0.02 III 0.04 UI
Nitrogen, Ammonia (HC/l) 0.55 I 0.0 I 0.21, I 0.31 I 3.6 I
Nitrogen, Total KJeldahl (HG/l) 0.96 III 0.57 N/J 10.1, I 5-.97 N/J 7.08 I
Phosphorus, Jotal (HG/l) 0.74 NI 0.26 N/J 3.23 NI 2.55 N/J 2.5 NI
Sulfate (HG/l) 180. I 170. I 92. I 90. I 102. I
Total Dissolved Solids (HG/l) 672. I 652. I 562. I 518. I 978. I
Nole: (1) Resul I s ore reported wi th qual it iers (lahoratory Ouallt ler/Date Val idot Ion OU811 fler) to the r 1911t 0# the value.
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ANALYTICAL DATA REPORT 5
Uoodstock landfill RI/FS
Uoods, tock Illinois
Matrix: GU Type: IND Hfl
P8rllllll!ter UK-GUHUO~D-D2 02/07/91 UK.GUHUO~D.92 02/07/91 UK.GUHUO~S-OI 11/01/90 UK.GUHUO~S.02 02/07/91 UK.GUHU050.01 11/01/90
-_.~-----_.._._-------_..._-.- ---------..-------------- ---...-.-------.------..-- [[[ ---......--...---------.. -.. --- ................... .. .... .. .. .. ..................
Alunlnun (UG/l) 50. UI 50. UI 200. UI 59. K/U 200. UI
Ant I many (UG/l) 5. UNI 5. UNI 50. UI 5. UNI 50. UI
Anenl c (UG/l) z. UI 2. UI 6.2 KI 9.6 KSI ~.2 KI
B8rhm WG/L> 210. I 20'. I 171. KI 150. KI 219. I
Berylliun (UG/l) 5. UI 5. UI 0.2 UI 5. UI 0.2 UI
C8dnhn (UG/l) 5. UI 5. UI 5. UI 5. UI 5. UI
C8ldun (UG/L) 161000. I 161000. I 132000. I 123000. I 111000. I
ChrOllllun, toUI (UG/l) 10. UI 10. UI 10. UI 10. UI 10. 1/1
Cobal t (UG/L) 10. UI 10. UI 50. UI 10. UI 50. HI
copper (UG/L) 10. UI 10. UI 10. UI 10. UI B. K/U
Iron (UG/l) 2770. I 2570. I 12600. I 12300. I ~92. I
le8d (UG/l) ]. UI 3. UI 3. HI ]. UI ]. UI
Magneslun (UG/l) 79000. I 79100. I ]1100. I ]1700. I 62700. I
Manganese (HG/l) ~22. I 1,22. I 598. I 615. I 85. I
Hercury (UG/l) 0.2 UI 0.2 UI 0.2 UI 0.2 UI 0.2 UI
Nlchl (UG/L> 20. UI 20. UI 20. UI 20. UI 20. UI
'Potasslun (HG/l) 2180. KI 211,0. KI ]6]0. KI 3570. KI 2]60. KI
Selenlun (UG/L) 2. USI 2. USI 2. 1/1 2. UI 2. UI
Sliver (UG/l) . 10. UI 10. UI 10. UN/R 10. UI 10. UN/R
SC)(tlun (UG/L) 62800. N/J 62200. N/J 17800. I 88900. N/J 26000. I
Thlliliun (UG/l) 3. U/ ]. ul 3. UI 3. UI ]. UI
Vllnedlun (UG/l) 50. UI 50. UI 2. UI 50. UI 2. UI
Zinc (UG/L) 1~. KI 10. UI 10. UI ]26. I 10. UI
Cyanide (UG/L> 10. UI 10. UI 10. UI 10. UI 10. U/
Alk811nlty, Totlll (HG/L> 712. I 611,. I 619. I 535. I ~85. I
Chloride (HG/l) 1~0. */J 138. */J 49. I 49. */J 31. I
Chemlc81 Oxygen Demand (HG/L) 1,5. IU 1,2. IU .117. IU
Nltr8te+Nltrlte Nitrogen (HG/l) 0.02 UI 0.02 UI 0.02 UI 0.08 IU 0.02 UI
Nitrogen, Ammonlll (HG/l) 3.1 I ~.~~ I 2.9 I 2;39 I 1.82 I
Nitrogen, Total Kjeldahl (HG/l) 7.02 N/J 7. N/J 15.1 I 11.7 N/J 1. 75 I
Phosphorus, Total (HG/l) 1.65 N/J 1.9] N/J 0.48 NI 0.39 N/J 0.05 NI
Sulf8te (HG/l) 108. I 106. I ]6. I M. I 77. I
Total Dissolved Solids (HG/l) 968. I 972. I 812. I 772. I 62~. I
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ANAlYJICAl DAJA REPORT 6
Uoodstock lendflll R I/fS
UOodstock, It I inois
Hetrix: Gli Jype: INO HTl
Parameter UK-GUHIlOSO-02 02/06191 UK-GUHU050-91 11/01/90 UK'CUHU05S-01 11/01/90 UK-GUHU05S-02 02/05/91 UK-GUHU060-01 11/02/90
.........-----...-.-..---------- -...------ ......e-___....--..... ------------------------ .... -..... --.............. --................ ......------ ----.. --"------.. -..-------.-..--.....--------
Alunlnun WC/l) 50. UI 200. UI 200. UI 50. UI 200. III
Ant lmony (Will) 5. UN I 50. UI 50. UI 5. UN I 50. III
Arsenic (UC/l) 2.9 KI 4.4 KI 4.3 KI 6.1 KSI 2. III
Bulun (UC/l) 235. I 229. I 3~~. I 311. I 333. I
Berylliun (UC/l) 5. UI 0.2 UI 0.2 UI S. UI 0.2 III
CI
-------
ANAlYIICAl DAIA REPORT 7
Uoodstock landfill RI/FS
Uoodstock. Illinois
Hatrix: GU Iype: IND MIL
Parameter UK.GUHU060-02 02/05/91 UK-CUHU06S-01 11/02/90 UK-GUHU06S-02 02/05/91 UK-GUHU07.01 02/06/91 UK-GUHU07-02 0"02/91
--..................- --.......... ......... ---.. ..........-...-.......--------..--- ........ eo......... -- -- -........ ----... --------..--------............ ................... ................................ .... .. ..... .. ...... .. ... ...... .. .. ............ ...
Ahmlnun (IIG/l) 50. III 200. III 50. III 57. KIll 51.5 KI
Antimony (IIG/l) 5. UNI 50. U/ 5. UNI 5. UNI 50. UI
Arseni c (UG/L> Z. IISI 2. IISI 2. IISI 11. I 19.Z I
Barllm (IIG/l) 337. I 174. KI 213. I 521. I 509. I
Beryl! hm (IIG/l) 5. III 0.2 II/ 5. III 5. III 5. III
Cadftlun (IIG/l) 5. UI 5. III 5. UI 5. III 5. UI
Calclun (UG/l) 160000. I 75800. I 95800. I 21'000. I 223000. /
Chromiun, total (IIG/l) 10. UI 10. III 10. UI 10. III 10. UI
Cobalt (IIG/l) 10. UI 50. III 10. III 10. III 10. III
Copper (IIG/l) 10. UI 11,. K/U 10. UI 10. UI 10. UI
Iron (IIG/l) 5]]0. I 20. III ]2. KIll 11600. I 11'00. I
lead (IIG/l) ]. III ]. USI ]. UI 3. UI ]. IISI
Hagnesiun (UG/l) 65500- 1 2HOO. I 32'00. / 111000. I 116000. I
Manganese (Uti/l) 391. I 92. I 206. I 507. / 597. /
Mercury (UG/l) 0.2 III 0.2 III 0.2 III 0.2 III 0.2 III
Nickel (UG/l) 20. III 20. III 21. KI 47. I 30.5 KI
Potassiun (UG/l) ]050. KI 2560. KI ]110. KI 861,0. I 8920. I
Selenlun (UG/l) 2. III 2. U/ 2. U/ 2. USI 2. USI
Sliver (UG/l) 10. UI 10. UN/R 10. III 10. UI 10. ul
Sodlun (IIG/L> 35500. N/J 18]000. I 175000. NI 93700. N/J 77500. I
Thailiun (UG/l) 3. UI 3. U/ ]. UI 3. U/ ]. USI
Vanadlun (UG/l) 50. III 2. USI 50. UI 50. UI 50. UI
Zinc (IIG/l) 1750. I 10. III 78. I 37. I 65.5 I
Cyanide (UG/l) 10. III 10. II/ 10. ul 10. III
Alkalinity, Total (HG/l) 303. I 1,31,. / "I,. / 769. I 985. I
Chloride (HG/l) 228. I 150. I 11,9. I 118. I 109. I
Chemical Oxygen Demand (MG/l) 20. III 20. III 60. III
Nltrate+Nltrite Nitrogen (HG/l) 0.21 IU 2.87 I 5.09 I 0.02 III 0.02 III
Nitrogen, Ammonia (MG/l) 2.11 I 0.1 III 0.15 I '6." I 8.96 N/J
Nitrogen, Total KJeldahl (MG/l) ].5 N/J 3.02 I 1." N/J ' 6.6 N/J 9.03' I
Phosphorus, Total (HG/l) 0.8 N/J 3.79 N/ 0.82 N/J 0.17 N/J 1.38 I
sulfate (HG/l) 111. I 80. I 80. I 11'. I 102. I
Total Dissolved Solids (HG/l) 76'. I 816. I 828. I \]00. I 13'0. I
Note: (I) Results ftre rcportcd with qualificls (ll1horatory QualifierlOata Validation Quail tier) to the right of the volue.
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ANALYTICAL DATA REPORT 8
Uoodstock lend'III Rl/fS
Uoodstock, Illinois
Hetrix: CU Type: INO HIl
Puemeter UK-CYHU08-01 02/11/91 UK-CYHU08-02 04/02/91 UK-GYHU09-01 02/11/91 UK-GYHU09-02 04/01/91 UK-GUHU09-91 02/11/91
.......~.-..----_...._-._._..- ..-.......... ..-.....----.........-. ----.-..----------------- ---....-........ ---....--------.. .... ----..-.. ...-.... ..---.... --...... ...... .... ...... .... .. ........ ...... .......... ..
Alunlnun (UG/l) 50. UI 50. UI 50. UI 68. KI 50. UI
Ant imany (UG/l) 5.1 KN/J 50. UI 5. UNI 50. UI 6.8 KN/J
Arsenl c (UG/l) 2. UI 2. UI 2. UI 2, UI 2. UI
Beriun (UG/l) 220. I 221. I 348. I 299. I 347. I
Beryl I iun (UG/l) 5. UI 5. UI 5. UI 5. UI 5. UI
Cectniun (UG/l) 5. UI 5. UI 5. UI 5. UI 5. UI
Cllclun (UG/l) 185000. I 188000. I 114000. I 121000. I 114000. I
Chromhm, tote I (UG/l) 10. UI 10. UI 10. UI 10. UI 10. UI
Cobll t (UG/L> 10. UI 10. UI 10. K/U 10. UI 10. UI
Copper (UG/l) 10. UI 10. UI 10. UI 10. UI 10. UI
Iron (UG/l) 5550. I 5040. I 5140. I 3130. I 5090. I
lead (UC/L) 3. UI 3. UI 3. UI 3. UI 3. UI
Hignesiun (UG/l) 102000. I 104000. I 47900. I 411900. I 47600. I
Hengenese (UG/L) 92. I 92. I 69. I 77.5 I 68. 1
Hercury (UG/l) 0.2 UI 0.2 UI 0.2 UI 0.2 UI 0.2 UI
Nickel (UG/l) 33. KI 25. KI 20. UI 20. UI 20. UI
potlsslun (UG/L) 2720. KI 2350. KI 2370. KI 2740. KI 2390. KI
Selenlun (UG/l) 2. UI 2. USI 2. UI 2. UI 2. UI
$11 ver (UG/l) 10. UI 10. UI 10. UI 10. UI 10; UI
Sodlun (UG/l) 70300. N/J 67800. I 84700. N/J 84600. I 84200. N/J
Theil lun (UG/l) 3. UI 3. USI 3. UI 3. USI 3. UI
Vlnldlun (UG/l) 50. UI 50. UI 50. UI 50. UI 50. UI
Zinc (UG/L) 37. I 16. KI 25. I 41.5 I 30. I
CYlnlde (UG/l) 10. UI 10. UI 10. UI
Alklllnlty, Tot81 (HG/I.) 862. I 868. I 588. I 565. I 570. I
Chloride (HG/l) 166. */J 151. I 117. */J 119. I 118. */J
Chemicil Oxygen Demend (HG/l) 45. IU 20. UI 20. UI
Nltrlte.Nltrlte Nitrogen (HG/l) 0.02 UI 0.02 UI 0.02 IU 0.02 UI 0.03 IU
Nitrogen, Ammonle (HG/l) 1.04 I 1.1 N/J 5.21 I 3.86 N/J 4.2] I
Nitrogen, Totll Kjeldahl (HG/l) 1.95 N/J 3.74 I 7.73 N/J ~.54 I 7.55 N/J
Phosphorus, Tot81 (HG/l) 0.39 N/J 1.98 I 0.31 N/J 0.65 I 0.29. N/J
Sui flte (HG/L> 34. I 35. I 32. I 38. 1 31. 1
Totll Dissolved Solids (HG/l) 1120. I 1080. I 740. I 776. I 740. I
Note: (1) Results ere reported lIith qualifiers (laboratory Quellfier/Data Volidotion Qualifier) to the right 01 the vallie.
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ANALYTICAL DATA REPORT 9
Uoodstock lendflll RI/FS
Uoodstock. Illinois
Hlltrix: GU Type: IND HIl
Parameter UK-GUHU09-92 0"01/91 UK-GUHUI0-01 02/07/91 UK-GUHUI0-02 04/01/91
..........------_.~----------- ---..--..-..-........ -.-........ -..- ------------..-..----..---- ------------------------
Ahnlnun (UG/l) 50. KI 81. "/U 72. KI
Antimony (UG/l) 50. UI 5. UNI 50. UI
Arsenic (UG/l) 2. UI 6.3 KI 6.1 KI
Barlun WG/l) 312. I 192. '" 166. KI
Beryllium (UG/l) 5. UI 5. UI 5. UI
Cadnlun (UG/l) 5. UI 5. UI 5. UI
Calelun (UG/l) 118000. I 192000. 1 165000. I
Chromium. total (IIG/l) 10. III 10. UI 10. III
Cobal t (UG/l) 10. III 10. UI 10. III
Copper (UG/l) 10. UI 10. UI 10. UI
Iron (UG/l) 1.790. I 19'00. 1 13400. I
leed (UG/l) 3. UI 3. USI 3. UI
Magnesium (UG/l) '9300. 1 53200. 1 '6300. I
Hanganese (UG/l) 69.5 I 708. 1 658. I
Mercury (UG/l) 0.2 UI 0.2 UI 0.2 UI
Nickel (UG/l) 20. UI 20. UI 20. UI
Potassium (UG/l) 23'0. KI 1260. KI 11.70. KI
Selenlun (UG/LJ 2. UI 2. UI 2. UI
Stiver (UG/l) 10. UI 10. UI 10. UI
Sodium (UG/l) 81700. I 19100. NI 20000. I
Thallium (UG/l) 3. UI 3. UI 3. UI
Vanadium (UG/LJ 50. UI 50. UI 50. UI
Zinc (UG/l) 10. KI 1'0. 1 38.5 I
Cyanide (UG/l) 10. UI
Alkalinity. Tot III (HG/l) 5'i6. I 899. 1 606. 1
Chloride (HG/l) 113. I 32. */J 2'. 1
Chemical Oxygen Demand (HG/l) 157. 1
Nltrate+Nltrite Nitrogen (HG/l) 0.02 UI 0.02 UI 0.0' UI
Nitrogen. Ammonia (HG/l) 3.95 N/J 3.28 I 3.67 N/J
Nitrogen. Total Kjeldahl (HG/l) 6.09 I 7.2' N/J 9.5 I
Phosphorus, Totel (HG/l) 1.18 I 0.51 !,/J 0.96 I
sutfate (HG/l) 31. I 51. I 46. I
Total Dissolved Solids (HG/l) 771.. I 916. I 794. I
Note: (I> Re~ults lire reported with qualifier~ (loboratory Quallfier/Date Validation Qualifier) to the right of the value.
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AN~lYrICAl DATA REPORT
Uoodstock landfill RI/FS
Uoodstock, illinois
Hatr Ix: GU Type: VOC
Generated by: CAY
Date Issued: 0r.'JIIN-91
Parameter UK'GUBBOI.01 11/02/90 UK-GUBB02-02 02/06/91 UK-GUfBOI.01 10/31/90 YK-GYfBOI-01 12/12/90 UK-GYfD02-01 11/02/90
.-....................--...... .......---............--- ----------------.------- ----------------....-.-- ---. -------........----- ---... -......--.-..-.-.------...--
Chloromethane (IIG/l) 10. II/ 10. II/ 10. II/ 10. II/ 10. II/
Bromomethane (IIC/l) 10. II/ 10. II/ 10. II/ 10. II/ 10. II/
Vinyl chloride (IIC/l) 10. II/ 10. II/ 10. II/ 10. II/ 10. II/
Chloroethane (IIC/l) 10. II/ 10. II/ 10. II/ 10. II/ 10. II/
Methylene chloride (IIC/l) 7. / 5. II/ 5. II/ 5. U/ 2. J/
Acetone (UC/l) 11. U/ 10. U/ 10. U/ 1'. B/UJ 10. II/
Carbon disulfide (UC/l) 5. II/ 5. II/ 5. II/ 5. II/ 5. U/
1,1-Dlchloroethene (IIC/l) 5. II/ 5. II/ 5. II/ 5. U/ 5. U/
1,1-0Ichloroethane (IIC/l) 5. II/ 5. III 5. II/ 5. II/ 5. II/
1,2-0Ichloroethene (total) (IIC/l) 5. II/ 5. U/ 5. II/ 5. II/ 5. II/
Chloroform (UC/l) 2. J/ 1. J/ 2. J/ 5. II/ 1. J/
1,2-0Ichloroethane (IIC/l) 2. J/ 5. II/ 5. II/ 5. II/ 5. II/
2-Butanone (IIC/l) 10. II/ 10. U/ 10. II/ 10. II/ 10. II/
1,1,I-Trlchloroethane (IIC/l) 5. II/ 5. U/ 5. II/ 5. II/ 5. II/
Carbon tetrachloride (UC/l) 5. II/ 5. U/ 1. J/ 5. U/ 5. II/
Vinyl acetate (UC/l) 10. U/ 10. U/ 10. II/ 10. U/ 10. II/
Bromodlchtoromethane (UC/l) 5. II/ 5. U/ 5. II/ 5. U/ 5. II!
1,2'Olchtoropropene (UC/l) 5. II/ 5. U/ 5. II/ 5. U/ 5. II/
cls.1,3-0Ichloropropene (UC/l) 5. II/ 5. U/ 5. U/ 5. II/ 5. II/
Trlchlorcathene(UG/I) 5. U/ 5. II/ 18. / 5. II/ 5. II/
Olbromochloromethane (UC/l) 5. U/ 5. U/ 5. U/ 5. II/ 5. II/
1,I,Z'Trlchloroethane (UC/l) 5. II/ 5. U/ 5. U/ 5. II/ 5. U/
Benzene (IIC/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. U/
trans'1,J-Olchloropropene (IIG/l) 5. U/ 5. II/ 5. II/ 5. II/ 5. II/
Bromoform (UC/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. II/
4-MethYI-2'pentanone (UC/l) 10. II/ 10. U/ 10. II/ 10. UI 10. II/
2-Nexanone (UC/l) 10. II/ 10. U/ 10. U/ 10. U/ 10. II/
Tetrachloroethene (IIC/l) 5. II/ 5. UI 5. U/ 5. II/ 5. II/
1,I,l,2-Tetrachloroethane (IIC/l) 5. II/ 5. UI 5. U/ 5. II/ 5. II/
Toluene (UC/l) 5. II/ 5. U/ 5. II/ 5. U/ 5. II/
Chlorobenzene (UC/l) 5. II/ 5. UI 5. II/ 5. U/ 5. II/
Ethylbenzene (!JC/l) 5. II/ 5. U/ 5. II/ 5. II/ 5. II/
Styrene (IIC/l) 5. II/ 5. U/ 5. U/ 5. II/ 5. II/
Xylene. (total) (IIC/I) 5. II/ 5. U/ 2. J/ 5. II/ 5. II/
Note:
-------
, .<
ANALYTICAL DATA REPORT 2
~oodstock Landfill Rl/fS
Uoods, toclc Illinois
Matrix: C~ Type: voe
Paremeter ~K-C~F006-02 02/01191 UK-CUf008.02 02/11/91 UK-CUFOI0-02 04/02/91 UK-GUHUOI0-01 12/12/90 UK-GUHUOI0-02 02/06/91
-.-.-.....--. -..--.."'.... -............ ....... ..---....-........ -- -- ........ .......-.. ------........--------..---.... ..-..---------..-..-----...-- ------------------------ .....-----------------..-..-
Chloromethane (UC/L) 10. UI 10. UI 10. UI 10. UI 10. UI
Bromomethane (UC/L) 10, UI 10. UI 10. UI 10- III 10. III
Vlnvl chloride (IIC/L) to. III 10. UI 10. UI 10. UI 10. UI
Chloroethane (UC/L) 10. UI 10. UI 10. UI 10. UI 10. UI
Methylene chloride (UC/L) 1. UI 6. UI 28. B/U 5. UI 1. UI
Acetone (UC/L) 10. UI 9. JI 10. UI 10. B/U 10. UI
Carbon disulfide (UC/L) 5. UI 5. UI 5. III 5. UI 5. UI
1,1-0Ichloroethene (UC/L) 5. UI 5. UI 5. UI 5. UI 5. UI
1,1-0Ichloroethane (UC/L) 5. UI 5. UI 5. UI 5. UI 5. UI
1,2-0Ichloroethene (total) (UG/L) 5. UI 5. UI 5. III 5; UI 5. UI
Chloroform (IIC/L) 5. UI 5. UI 5. III 5. UI 5. UI
1,2-0Ichloroethane (UC/L) 5. UI 5. UI 5. UI 5. UI 5. UI
2'Butanone (UC/l) 10. UI 10. UI 10; UI 10. UI 10. UI
1,1,I-Trlchloroethane (UG/L) 5. UI 5. UI 5. III 5. UI 5. UI
Carbon tetrachloride (UC/L) 5. UI 5. UI 5. UI 5. UI 5- UI
Vinyl acet.te (UC/l) 10. III 10. UI 10. UI 10. UI 10. UI
Bromodlchloromethane (UG/l) 5. UI 5. UI 5. UI 5. UI 5. UI
1,2'Olchloropropane (IIC/L) 5. UI 5. UI 5. UI 5. UI 5. III
cl,'1,3'Olchloropropene (UC/L) 5. UI 5. UI 5. UI 5. UI 5. UI
Trlchloroethene (UC/l) 5. UI 5. UI 5. UI 5. UI 5. U/
Olbromochtoromethane (UG/l) 5. UI 5. UI 5. UI 5. UI 5. UI
1,1,Z-Trlchtoroethane (UC/L) 5. UI 5. UI 5. III 5. III 5. UI
Benzene (UC/l) 5. UI 5. UI 5. UI 5. UI 5. UI
trans-I,3-0Ichloropropene (UG/l) 5. UI 5. UI 5. UI 5- III 5. III
Bromoform (UG/l) 5. UI 5. UI 5. UI 5. UI 5- UI
"Methyl'2-pentanone (UC/l) 10. UI 10. UI 10. UI 10. UI 10. UI
2'Hexanone (Ur./l) 10. UI 10. UI 10. UI 10. UI 10. UI
Tetrachloroethene (UG/L) 5. UI 5. UI 5. UI 5. UI 5. UI
1,1,2,2-Tetrachloroethane (UC/l) 5. UI 5. UI 5. UI 5. UI 5. UI
Toluene (UC/l) 5. UI 5. UI 5. UI 5. UI 5. III
Chlorobenzene (UC/L) 5- III 5. UI 5. UI 5. UI 5. III
Ethytbenzene (UC/l) 5. UI 5. UI 5. UI 5. UI 5. UI
Styrene (IIG/l) 5. III 5. UI 5. UI 5. UI 5. UI
Xylenes (total) (UG/l) 5. UI 5. UI 5. UI 5. UI 5. UI
Note: (1) Results are reported \lith qunlifiers (lahorotory Qualifier/Olita Validation Qualifier) to the right 01 the vnlue-
-------
ANALYTICAL DATA REPORT 3
Uoodstock Lendflll RllfS
UOodstock, Illinois
Hetrix: CII Type: VOC
Peremeter UK-C~U01S-01 10/31/90 UK-CUHU01s-02 02/06191 UK-CUHU02D-OI 12/12/90 UK-CUHU02D-02 02/06191 UK-CUHU02S-01 10/31/90
-.-.............-----....--..---- -.-.--------.-----.----- .-----------------..-..-.. -...... --..- .... ........ --.. -..... ---------...------------ .... --..................... --..'O.. -.......
Chloromethane (UC/L) 10. UI 10. UI 10. UI 10. U/ 10. UI
Bromomethane (UC/l) 10. UI 10. UI 10. UI 10. UI 10. III
Vinyl chloride (UC/l) 10. UI 10. UI 10. UI 10. UI 10. UI
Chloroethane (UC/l) 10. UI 10. UI 10. UI 10. UI 10. UI
Methylene chloride (UC/l) 5. UI 9. UI 5. UI 5. UI 5. UI
Acetone (UC/l) 10. UI 10. UI 10. 8/U 10. UI 10. III
Carbon disulfide (UC/l) 5. UI 5. III 5. III 5- III 5. III
1,1'Olchloroethene (UG/l) 5. III 5. UI 5. UI 5. UI 5. III
1,1'0Ichloroethene (UC/L) 5. UI 5. UI 5. UI 5. UI 5. UI
1,2-0Ichloroethene (totel) (UC/l) 5. UI 5. UI 5. UI 5. UI 5. UI
Chloroform (UC/l) 5. UI 5. III 5. UI 5. UI 5. III
1,2-0Ichloroethane (IIG/l) 5. UI 5. UI 5. UI 5. UI 5. III
2-Butenone (UG/l) 10. III 10. UI 10. III 10- UI 10- UI
1,1,1-Trlchloroethane (UC/l) 5. UI 5. UI 5. UI 5. UI 5. III
Carbon tetrachloride (UC/l) 5. UI 5. UI 5. UI 5. UI 5- UI
Vinyl acetate (IIC/l) 10. III 10. UI 10. III 10. III 10. II/
Bromodlchloromethane (IIC/l) 5. UI 5. UI 5. III 5. III 5. UI
1,2-0Ichloropropane (IIG/l) 5. III '. UI 5. III 5. UI 5. UI
cls-1,]-Olchloropropene (UG/l) 5. UI 5. UI 5. III 5. III 5. III
Trlchloroethene (UG/l) 5. UI 5. UI 5. III 5. UI 5. III
Dlbromochloromethane (IIC/l) 5. UI 5. UI 5. III 5. III 5. U/
1,I,2'Trlchloroethane (UC/l) 5. UI 5. UI 5. UI 5. UI 5. UI
Benzene (UG/l) 2. JI 5. UI 5. UI 5. III 5. UI
trans'1,]-Dlchloropropene (UC/l) 5. UI 5. III 5. U/- 5. U/ 5. UI
Bromoform (IIC/l) 5. UI 5. UI 5. UI 5. III 5. III
4-Hethyt-2-pentenone (UC/l) 10. III 10. UI 10. UI 10. UI 10. UI
2-Ke.anone (UG/l) 10. UI 10. UI 10. UI 10. UI 10. U/
Jetrechloroethene (UG/l) 5. UI 5. U/ 5. UI 5. UI 5. U/
1,1,2,2'Tetrachloroethane (UG/l) 5. II/ 5. U/ 5. U/ 5. UI 5. UI
Toluene (UG/L> 5. U/ 5. UI 5. UI 5. UI 5. U/
Chlorobenzene (UC/l) 2. J/ 5. UI 5. U/ 5. UI 5. III
Ethylbenzene (IIC/l) 5. II/ 5. II/ 5. III 5. U/ 5. II/
Styrene (UC/l) 5. II/ 5. II/ 5. IJ/ 5. U/ 5. U/
Xylenes (total) (IIC/l) 5. III 5. UI 5. U/ 5. UI 5. II/
Note: (1) Results ore reported with quolifiers (I nhorotory Qualifier/Date Validation Qualifier) to the right of the vAlue.
, '.
" ,
-------
,<
ANAlYJICAl DATA REPORJ 4
Uoodstock landfill Rl/fS
Uoodstock, illinois
Hatrlx: GU Type: vac
Perameter UK.GUHU02S-02 02/06191 UK-GUH~2S.91 10/31/90 UK-GUHUOJO-OI 11/01/90 ur.GUHU03D-02 02/06/91 UI(-GUHUOJS-OI 11/01/90
--...........-......---... -...........-........ &........ ................ .......... .............................. -----.-..-------...------...- -----------------...----- ......--..............---.....-..------ --------....---..-.--------
Chloromethane (UG/l) 10. III 10. UI 10. III 10. UI 10. UI
Bromomethene (UG/l) 10. UI 10. UI 10. UI 10. UI 10. UI
Vinyl chloride (UG/l) 111. UI 10. UI 1(). UI 10. UI 10. UI
Chloroethene (UG/l) 10. UI 10. UI 10. UI 10. UI 10. III
Methylene chloride (UG/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. lI/
Acetone (UG/l) 10. UI 10. UI 10. UI 10. UI 10. lI/
Carbon disulfide (UG/l) 5. UI 5. UI 5. III 5. UI 5. III
1,1-0ichloroethene (lIG/l) 5. III 5. UI 5. III 5. UI 5. III
1,1-0lchloroethane (lIG/l) 5. III 5. III 5. III 5. UI 5. III
1,2-0ichloroethene (total) CUG/l) 5. UI 5. III 5. III 5. III 5. lI/
Chloroform (lIG/l) 5. UI 5- III 5. UI 5. lI/ 5. lI/
1,2-0lchloroethane (lIG/l) 5. U/ 5. UI 5. UI 5. III 5. lI/
2'Butanone (UG/l) 10. III 10. III 10. UI 10. UI 10. III
1,I,1-Jrlchloroethane (UG/l) 5. III 5. UI 5. UI 5. UI 5. lI/
Carbon tetrachloride (lIG/L) 5. UI 5. UI 5. UI 5. III 5. lI/
Vinyl acetate (lIG/l) 10. III 10- UI 10. III 10. III 10. lI/
Bromodlchloromethene (lIG/l) 5. III 5. UI 5. UI 5. UI 5. UI
1,2-Dlchloropropene (UG/l) 5. III 5. UI 5. III 5. UI 5. U/
cls.1,J.Dlchloropropene (UG/l) 5. III 5. UI 5. lI/ 5. lI/ 5. III
Jrlchloroethene (lIG/l) 5. III 5. UI 5. III 5. III 5. UI
Olbromochloromethene (lIG/l) 5. III 5. III 5. III 5. UI 5. lI/
1,1,2'Jrlchloroethane (lIG/l) 5. III 5. III 5. III 5. III 5. III
Benzene (lIG/l) 5. III 5. III 5. III 5. III 5. III
trans-1,3.Dlchloropropene (UG/l) 5. III 5. III 5. lI/ 5. III 5. III
BromoforM (lIG/l) 5. lI/ 5. UI 5. III 5. III 5. U/
4-Hethyl-2-pentanone (UG/l) 10. UI 10. UI 10. UI 10. UI 10. lI/
2-Hexanone (UG/l) 10. III 10. UI 10. III 10. III 10. lI/
Jetrachloroethene (lIG/l) 5. III 5. III 5. lI/ 5. III 5. lI/
1,1,Z,Z.Jetrachloroethane (lIG/l) 5. lI/ 5. UI 5. UI ~. UI 5. III
Joluene (UG/l) 5. III 5. UI 5. III "5. UI 5. III
Chlorobenzene (UG/l) 5. lI/ 5. UI 5. III 5. III 5. U/
Ethylbenrene (lIG/l) 5. III 5. UI 5. U/ 5. III 5. lI/
Styrene (lIG/l) 5. III 5. UI 5. III 5. III 5. III
Xylenes (total) (lIG/L) 5. III 5. UI 5. III 5. III 5. III
Note: (1) Results ore reported with qualifiers (loboratory Qualifier/Deta Validation Qualifier) to the right of the value.
-------
ANALYTICAL DATA REPORT S
Voodstock landfill RI/FS
Uoodstock, Illinois
Matrix: GII Type: vac
Parameter IIK-6I1HII03S-02 02/06/91 VK-GUHVO~D-OI 11/01/90 UK-6UHVO~D.OZ 02/07/91 VK-GUHUO~D.92 02/07/91 UK'GUHUO~S'OI 11/01/90
-..-_..~----._---------------- ------------------------ ----.-.-----..---.------ .-.---.... --. --.........-.. ...e..... ... .........-- - --.. .....---. -.. - - -. .. -------.. --.. ----.... "----..
Chloromethane (UG/l) 10. UI 10. UI 10. UI 10. U/ 10. II/
Bromomethane (UC/l) 10. UI 10. UI 10. U/ 10. UI 10. III
Vinyl chloride (UG/l) 10. U/ 16. I 21. / 1~. / 10. U/
Chloroethane (Ua/l) 10. UI 10. UI 10. UI 10. U/ 10. U/
Methylene chloride (UG/l) 5. UI 5. U/ 6. UI 5. UI 5. U/
Acetone (UG/l) 10. UI 10. UI 10. UI 10. U/ 10. UI
Carbon dlsul fide (1l6/l) 5. UI 5. UI 5. U/ 5. U/ S. U/
1,1'0lchloroethene (U6/l) 5. UI 5. UI 5. UI 5. UI S. UI
1,1-0lchloroethane (U6/l) 5. UI 5. UI 5. UI 5. UI 5. UI
1,2-0lchloroethene (total) (UG/l) 5. UI 5. U/ 5. U/ 5. U/ 5. UI
Chloroform (UG/l) 5. U/ 5. UI 5. u/ 5. U/ 5. UI
1,2'Dlchloroethane (UG/l) 5. U/ 5. UI 5. UI 5. UI 5. UI
2'Butanone (U6/L) 10. III 10. U/ 10. III 10. UI 10. III
1,1,1'Trlchloroethane (U6/l) 5. 11/ 5. U/ 5. 11/ 5. III 5. 11/
Carbon tetrlchlorlde (U6/L) 5. U/ 5. III 5. UI 5. III 5. 11/
Vlnvl Icetate (UG/l) 10. U/ 10. U/ 10. 11/ 10. UI 10. III
Bromodlchloromethane (UG/L) 5. 11/ 5. U/ 5. UI 5. UI 5. UI
1,2-Dlchloropropane (U6/L) 5. U/ 5. U/ 5. UI 5. U/ 5. UI
cls-1,3-Dlchloropropene (U6/L) 5. UI 5. 11/ 5. UI 5. III 5. III
Trlchloroethene (UG/l) 5. 11/ 5. UI 5. UI 5. III 5. 11/
Dlbromochloromethane (UG/l) 5. 11/ 5. U/ 5. U/ 5. UI 5. III
1,I,Z-Trlchloroethane (UG/l) 5. U/ 5. U/ 5. UI 5. U/ 5. 11/
Benzene (UG/l) 5. U/ 5. UI 5. III 5. UI 5. UI
trlns-1,3-Dlchloropropene (IlG/l) 5. 11/ 5. UI 5. u/ 5. U/ 5. U/
Bromoform (UG/l) 5. 11/ 5. UI 5. UI 5. U/ 5. UI
"MethVI-2-pentlnone (UG/l) 10. 11/ 10. UI 10. UI 10. U/ 10. UI
2'Hexanone (UG/l) 10. U/ 10. UI 10. UI 10. U/ 10. UI
Tetrlchloroethene (UG/l) 5. 11/ 5. UI 5. UI 5. UI 5. U/
1,1,2,2'Tetrachloroethane (UG/l) 5. III 5. UI 5. U/ 5. III 5. U/
Toluene (U6/l) 5. III 5. u/ 5. UI 5. . UI 5. UI
Chlorobenzene (UG/l) 5. III 5. UI 5. III 5. UI 5. u/
Ethvlbenzene (U6/l) 5. 11/ 5. 11/ 5. 11/ 5. UI 5. UI
Styrene (U6/l) 5. 11/ 5. U/ 5. U/ 5. UI 5. U/
Xylenes (total) (UG/l) 5. 11/ 5. U/ 5. UI 5. U/ 5. U/
Note: (1) Results are rl'ported with qualifiers (l.oboratory Oualifier/Data Validation Ouollfler) to the right 01 the yolue.
'.
., ,
-------
I I ~
ANAlYJICAl OAJA AEPORJ 6
Uoodstock landfIll RI/FS
Uoodstock, Illinois
Hatrlx: GU Jype; VOC
Parlll1leter UK-GUHU04S-02 02/07191 UK-GUHU050-01 12112/90 UK-GUHU050-02 02/06/91 UK-GUHU050-91 12/12/90 UIC-GUHU05S-01 11/01/90
....-. "--oO ............ ---""""oO"""""" - ................oO"""" ......... ........... .....................--...........................-... "'-""'''''''.'''''.'''---.''oO'''''''''--'' -.... -......... -......... -............ -oO -.. - - - -............ ........ - .. ........ ........ ..
Chloromethane (UG/l) 10. UI 10. UI 10- UI 10. U/ 10. u/
Bromomethane (UG/l) 10. UI 10. UI 10. UI 10. UI 10. UI
Vinyl chloride (UG/l) '0. UI 10. UI 10. UI 10. UI 10. III
Chloroethane (UG/l) 10. UI 10. UI 10. UI 10. U/ 10. U/
Hethylene chloride (UG/l) 11. UI 5. U/ 5. UI 6. B/U 5. UI
Acetone (UG/l) 10. UI 10. UI 7. J/U 10. UI 10. UI
Carbon disulfide (UG/l) 5. UI 5. UI 5. UI 5. UI 5. UI
1,1-0lehloroethene (UG/l) 5. UI 5. UI 5. UI 5. UI 5. III
1,1-0ichloroethane (UG/l) 5. UI 5. UI 5. U/ 5. UI 5. II/
1,2-0lchloroethene (total) (UG/l) 5. U/ 5. UI 5. III 5. UI 5. ul
Chloroform (UG/l) 5. UI 5. UI 5. UI 5. UI 5. UI
1,2'Diehloroethane (UG/l) 5. UI 5. UI 5. U/ 5. U/ 5. UI
2-Butanone (UG/l) 10. UI 10. U/ 10. U/ 10. UI 10. ul
1,1,1.Jriehloroethane (IIG/l) 5. U/ 5. UI 5. UI 5. UI 5. UI
Cerbon tetreehlorlde (UG/l) 5. UI 5. UI 5. UI 5. UI 5. UI
Vinyl eeetete (UG/L) 10. UI 10. UI 10. UI 10. U/ 10- UI
Bromodichloromethane (UG/L) 5. UI 5. U/ 5. U/ 5. U/ 5. U/
1,2-0lchloropropane (UG/l) 5. UI 5. UI 5. UI 5. UI 5. UI
cls'I.3-0Ichloropropene (UG/L) 5. UI 5. UI 5. UI 5. UI 5. UI
Jrlchloroethene (UG/L) 5. UI 5. UI 5. UI 5. U/ 5. UI
Olbromoehloromethane (UG/L) 5. U/ 5. UI 5. UI 5. UI 5. U/,
1.1,2'Jrlchloroethane (UG/l) 5. U/ 5. UI 5. UI 5. UI 5. UI
Benzene (UG/L) 5. UI 5. UI 5. UI 5. UI 4. J/
trens-1,]-Oiehloropropene (UG/l) 5. UI 5. UI 5. UI 5. ul 5. U/
Bromoform (UG/l) 5. UI 5. UI 5. UI 5. UI 5. UI
4'Hethyl-2-pentenone (UG/l) 10. UI 10. UI 10. UI 10. UI 10. UI
2'Mexenone (UG/l) 10. UI 10. U/ 10. UI 10. UI 10. UI
Tetrechloroethene (UG/l) 5. UI 5. UI 5. UI 5. U/ 5. UI
1,1,2,2-Tetrachloroethene (UG/L> 5. UI 5. U/ 5. UI 5~ UI 5. UI
Joluene (UG/l) 5. UI 5. UI 5. UI 5. UI 5. III
Chlorobenlene (UG/l) 5. UI 5. U/ 5. U/ 5. UI 5. II/
Ethylbenlene (UG/l) 5. III 5. UI 5. U/ 5. UI 5. UI
Styrene (UG/l) 5. UI 5. UI 5. UI 5. UI 5. UI
Xylenes (total) (UG/l) 5. U/ 5. U/ 5. UI 5. III 5. U/
Note: (1) Results are reported with qualifiers (lahoratory Quelltler/Oata Validation Qualifier) to the right 01 the value.
-------
~M~lYTtC~l O~T~ REPORT 7
Uoodstock landfill RtlfS
Uoodstock, t H inols
: GU Type: vac
eter UK-GUHU05S-0Z 02/05/91 UK-GUHU060-01 12/12/90 UK-GUHU060-02 02/05/91 UK-GUHU06S-01 11/02/90 UK-GUHU06S-02 02/05/91
-..--...--..------------- .-...-....................-- ...---..-...--...-----.-----. ---...----............ ......-"",,- --.. ..------..-..-------------- - .. ..... ........ .. .. - . .. .. - - .. ............ ..
-ocnethane (UG/l) 10. UI 10. UI 10. UI 10. UI 10. UI
)llll!thane (UG/l) 10. UI 10. UI 10. UI 10. UI . 10. UI
t chtoride (UG/l) 10. UI 10. UI 10. \II 10. UI 10. UI
roe thane (UG/l) 10. UI 10. UI 10. UI 10. UI 10. UI
Iylene chloride (UG/l) 5. UI 5. UI 5. UI 5. UfUJ 5. UI
tone (UG/l) 10. UI 10. UI 9. JfU 10. UI 11. fU
bon dlsu\fide (UG/l) 5. UI 5. UI 5. UI 5. UI 5. UI
-Olch\oroethene (UG/l) 5. UI 5. U/ 5. UI 5. UI 5. HI
,-O\ch\oroethane (UG/l) 5. UI 5. U/ 5. U/ 5. UI 5. HI
l-Olch\oroethene (tota\) (UG/l) 5. UI 5. U/ 5. U/ 5. U/ 5. III
\oroform (UG/l) 5. UI 5. UI 5. UI 5. UI 5. UI
2-0lchtoroethane (UG/l) 5. ul 5. UI 5. UI 5. U/ 5. UI
Butanone (UG/l) 10. UI 10. H/ 10. UI ,o. UI ,o. UI
.1,1-Trichloroethane (UG/l) 5. UI 5. ul 5. UI 5. UI 5. UI
.rbon tetrach\orlde (UG/l) 5. UI 5. UI 5. UI 5. UI 5. UI
Inyt acetate (UG/l) 'o. U/ \0. U/ 10. UI '0. UI 10. HI
,romodlcMoromethall8 (UG/l) 5. UI 5. U/ 5. UI 5. UI 5. UI
1,2-0ich\orOpropane (UG/l) 5. UI 5. U/ 5. UI 5. UI 5. UI
:\.-1,3,Oich\OrOpropene (UG/l) 5. UI 5. U/ 5. UI 5. U/ 5. \II
Trich\oroethene (UG/l) 5. UI 5. UI 5. UI 5. U/ 5. UI
Olbromochtoromethane (UG/l) 5. UI 5. UI 5. UI 5. UI 5. U/
,,1,2-Trlch\oroethane (UG/l) 5. UI 5. UI 5. UI 5. UI 5. UI
Benzene (UG/l) J. J/ 5. UI 2. J/ 5. UI 5. ul
trans-1,3-0ich\Oropropene (UG/l) 5. UI 5. U/ 5. U/- 5. UI 5. UI
Bromoform (UG/l) 5. U/ 5. U/ 5. UI 5. UI 5. UI
~-"ethy\-2-pentanone (UG/l) 10. U/ 10. UI \0. U/ 10. UI 10. UI
2-HeKanone (UG/l) 10. U/ 10. UI 10. ul '0. U/ 10. ul
Tetrach\oroethene (UG/l) 5. U/ 5. U/ 5. UI 5. U/ 5. UI
1,1,2,2-TetraCh\Oroethane (UG/l) 5. U/ 5. U/ 5. U/ 5. UI S. UI
Toluene (UG/l) 5. U/ 5. U/ J. J/ 5. U/ 5. UI
ch\orobentene (UG/l) 5. UI S. U/ 5. U/ 5- U/ 5. U/
Ethy\bentene (UG/l) 5. u/ 5. UI 5. UI 5. U/ 5. ul
styrene (UG/l) 5. U/ 5. u/ 5. UI 5. U/ 5. UI
Xy\enes (tot81) (UG/l) 5. U/ 5. U/ 5- UI 5- U/ 5. UI
. n"ftl \fier/Oata validation QlIa\ !fier) to the right of the value-
, '.
!I,
-------
, "
ANALYTICAL DATA REPORT 8
Uoodstock landfill RI/fS
lIoodstock, III inots
"atrix: GII Type: vac
Parameter IIK-GIIHII07-01 02/06/91 UK-GIIHII07-02 04/02/91 UK-GIIHII08-01 02/11/91 UK-GIIHII08-02 04/02/91 IIK-GIIHII09-01 02/11/91
....................... .... ...... .......... .... ...... .... .. .. .... ........ .. .. .. ...... .. .. ............ ........ .................-......-----..----.. ...--......-------........_--_.._- .. - .............. ....................... .. .. .... .... ............ .. .. .... .. ... .. .. ............ .. ..
Chloromethene (UG/l) 10. U/ 10. U/ 10. U/ 10. U/ 10. U/
Bromomethene (UG/l) 10. U/ 10. U/ 10. ul 10. U/ 10. U/
Vinyl chloride (UG/l) 10, U/ 10. U/ 21. / 20. / 10. U/
Chloroethane (\JG/I.) 10. UI 10. U/ 10. \J/ 10. U/ 10. \JI
"ethylene chloride (UG/l) 5. U/ 18. R/U 6. U/ 35. /U 5. UI
Acetone (UG/l) 5. J/ 10. U/ 10. U/ 10. U/ 10. UI
Carbon disulfide (UG/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. U/
1,1'Dlchloroethene (UG/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. U/
1,l'Olchloroethane (UG/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. U/
1,2-0lchloroethene (totel) (UG/l) 5. U/ 5. U/ 2. J/ 3. J/ 5. U/
Chloroform (UG/l) 5. U/ 5. U/ 5. U/ 5. UI 5. UI
1,2'Dichloroethene (UG/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. U/
2-Butanone (UG/l) 10. U/ 10. U/ 10. \J/ 10. U/ 10. U/
1,I,I-Trlchloroethane (UG/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. U/
Carbon tetrachloride (UG/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. U/
Vinyl acetate (UG/l) 10. U/ 10. U/ 10. U/ 10. U/ 10. u/
Bromodlchloromethene (UG/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. U/
1,2-0lchloropropene (UG/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. II/
cls'I,]'Dlchloropropene (UG/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. \J/
Trlchloroethene (UG/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. U/
Olbromochloromethane (UG/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. II/
1,I,2-Trlchloroethene (UG/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. U/
Benzene (UG/l) 4. J/ 4. J/ 5. U/ 5. U/ 5. U/
trans-1,]'0Ichloropropene (UG/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. U/
Bromoform (UG/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. U/
4-Hethyl'2-pentanone (UG/l) 10. U/ 10. U/ 10. U/ 10. U/ 10. U/
2.Hexanone (UG/l) 10. \1/ 10. U/ 10. U/ 10. U/ 10. U/
Tetrachloroethene (UG/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. UI
1,I,2,2'Tetrechloroethane (UG/l) 5. II/ 5. U/ 5. U/ 5. U/ 5. \J/
Toluene (UG/l) 5. U/ 5. U/ 5. UI 5. U/ 5. U/
Chlorobenzene (UG/l) 5. \J/ 5. U/ 5. U/ 5. U/ 5. U/
Ethylbenzene (UG/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. U/
Styrene (UG/l) 5. \J/ 5. U/ 5. U/ 5. U/ 5. U/
Xylenes (totel) (UG/l) 5. UI 5. U/ 5. U/ 5. UI 5. U/
Note: (1) Results are reported with qualifiers (laboratory Qualifier/Date Validlltion Qualifier) to the right ot the value.
-------
~H~lY1ICAl 0~1~ REPOR1 9
Yoodstock landfill RI/fS
yoodstock, III Inol&
II: G\I 1ype: VOC
meter UK-GWMW09-02 0~/0'/91 \/K-GYHU09-9' 02/11/91 \/K-GYHU09-9Z O~/0'/9\ UK.GUHU10-01 02/07/9\ YK-GUHY10.02 0~/01/9'
..... ",-.........-..",.. ..-..-"'-" ....... ............................. ...--........--.-..--.............-- .......---......... - --- ......",- ......-.... --......-----.....--------...... -...... ........ .. .. .. .. - ...", .. - -..........."
Iromethane (UG/l) \0. U/ '0. U/ 10. U/ \0. U/ \0. III
nomethane (UG/l) 10. U/ 10. U/ \0. U/ \0. U/ 10. UI
Vi chloride (UG/l) 10. U/ \0. U/ \0. U/ '0. U/ 10. u/
oroethane (UG/l) \0. U/ '0. U/ '0. U/ '0. U/ \0. U/
:hylene chloride (UG/l) \7. B/U S. U/ 11. BN S. U/ 12. 8/U
!tone (UG/l) 'O. U/ 10. U/ '0. U/ '0. /U 'O. U/
rbon disulfide (UG/l) 5. U/ S. U/ S. U/ S. U/ S. UI
,.0'chloroethene (UG/l) 5. U/ 5. U/ S. U/ S. U/ S. U/
.1-0Ichloroethane (UG/l) S. U/ 5. U/ 5. U/ S. U/ S. UI
,2-0lchloroethene (total) (UG/l) S. UI S. U/ 5. U/ 5. U/ S. U/
hloro'orm (UG/L) 5. UI 5. U/ S. U/ S. U/ 5. UI
,Z-Olchloroethane (UG/l) 5. U/ 5. U/ 5. U/ S. U/ S. U/
:.8uunone (UG/l) 'O. U/ 'O. U/ '0. U/ 'O. UI \0. UI
1,\,1.trlchloroethane (UG/l) 5. U/ S. U/ S. U/ 5. U/ '). U/
:arbon tetrachloride (UG/l) S. U/ 5. u/ S. U/ S. U/ S. UI
Vinyl acetate (UG/l) \0. U/ '0. U/ '0. UI '0. U/ 'O. UI
8romodlchloromethane (UG/l) 5. U/ S. U/ 5. U/ 5. U/ S. UI
1,2-0lchloropropane (UG/\) S. U/ 5. U/ 5. U/ 5. U/ 5. U/
cls-1,)-Olchloropropene (UG/l) 5. U/ S. U/ S. U/ S. U/ 5. U/
trlchloroethene (UG/l) s. U/ 5. U/ 5. U/ S. U/ 5. U/
Olbromochloromethane (UG/l) 5. U/ 5. U/ 5. U/ 5. U/ S. UI
1,1,2-trlchloroethane (UG/l) 5. U/ S. U/ 5. U/ S. U/ S. UI
Benzene (UG/l) 5. U/ 5. U/ S. U/ S. U/ 5. UI
tran..,,3-0Ichloropropene (UG/l) S. U/ S. U/ 5. U/ S. u/ S. UI
Bromoform (UG/l) S. U/ S. U/ S. U/ 5. U/ 5. U/
~-"ethyl.2.pentanone (UG/l) '0. U/ \0. U/ '0. ii/ '0. U/ '0. U/
2-NeKanane (UG/l) '0. U/ '0. U/ '0. U/ '0. U/ 10. U/
tetrach\oroethene (UG/\) 5. U/ 5. U/ 5. U/ 5. U/ 5. UI
1,1,2,Z-1etrachloroethane (UG/L) 5. U/ 5. U/ S. U/ S. U/ S. U/
101uene (UG/l) 5. U/ S. U/ S. U/ S. U/ S. U/
chlorobenzene (UG/l) 5. U/ 5. U/ S. U/ 5. U/ S. U/
Ethylbenzene (UG/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. UI
styrene (UG/l) S. U/ S. U/ 5. UI 5. U/ 5. U/
xylene' (total) (UG/l) 5. U/ 5. U/ S. U/ 5- U/ 5. U/
..-... ollalifier/08t8 validation Qualifier) to the right 0' the velue.
, '.
, ,
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ANALYTICAL DATA REPORT 10
Voodstock landfill RiffS
Voodstock, !ltinols
Matrix: GIJ Type: VOt
Parameter UK-GUIOOI-OI 10/31/90 UK-GUTOOI-01 12/12/90 UK-GIJT002-01 10/31/90 UK-GUI003-01 11/02/90 UK-G\JIOO~-02 02/05/91
--................"'''''''--- --- -- .--..- ---- _........--- -... ----.. ----- ---.... ----------"'..._---"'----..-.. ................... ... ............................ ...... ..................... ................ ...... .. .... .... ................. ...... .. .. .. .. .. .... ........ ....
Chloromethane (IlG/l) 10. II/ 10. II/ 10. II/ 10. II/ 10. III
Bromomethane (IIC/l) '0. III 10. III 10. II/ 10. II/ 10. U/
Vinyl chloride (UG/l) '0. UI 10. UI 10. U/ 10. UI '0. UI
Chloroethane (UG/I) 10. U/ 10. UI 10. U/ 10. U/ 10. UI
Methylene chloride (UC/l) 5. UI 5. II/ 5. U/ 5. U/ 5. UI
Acetone (IIC/l) 10. U/ 12. B/UJ 10. U/ 10- U/ 12. O/U
Carbon disulfide (UC/l) 5. UI 5. UI 5. UI 5. U/ 5. UI
1,1-0lchloroethene (UC/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. UI
1,1-0lchloroethane (UC/l) 5. U/ 5. U/ 5. II/ 5. U/ 5. U/
1,2-0lchloroethene (total) (IIC/l) 5. U/ 5. U/ 5. U/ 5. UI 5. U/
Chloroform (UG/l) 2. J/ 1. J/ 2. J/ 2. J/ 1. JI
I,Z-Olchloroethane (UC/l) 5. U/ 5. U/ 5. UI 5. UI 5. UI
2-Butanone (UC/l) 10. II/ 10. U/ 10. II/ 10. U/ 10. U/
1,1,l'Trlchloroethane (UC/l) 5. II/ 5. U/ 5. U/ 5. UI 5. UI
Carbon tetrachloride (UC/l) 5. U/ 5. U/ 5. U/ 5. U/ 5- III
Vinyl acetate (UC/l) 10. UI 10. U/ 10. UI 10. U/ 10. III
Bromodichloromethane (UC/l) 5. II/ 5. II/ 5. II/ 5. II/ 5. U/
1,2-Dlchloropropane (UC/l) 5. II/ 5- U/ 5. UI 5. III 5. U/
cis-I,3-0ichloropropene (UC/l) 5. U/ 5. U/ 5. UI 5. UI 5. UI
Trlchloroethene (UG/l) 5. UI 5. U/ 5. UI 5. UI 5. UI
Dlbromochloromethane (UC/l) 5. U/ 5. II/ 5. II/ 5. II/ 5. II/
1,1,2'Trlchloroethane (UC/l) 5. U/ 5. U/ 5. U/ 5. II/ 5. UI
Benzene (UG/l) 5. U/ 5. U/ 5. U/ 5. II/ 5. U/
trans'I,3-0Ichloropropene (UC/l) 5. U/ 5. U/ 5. II/ 5. U/ 5. U/
Bromoform (UC/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. U/
4'Methyl'2-pentanone (UG/l) 10. U/ 10. U/ 10. U/ 10. UI 10. UI
2'Hexanone (UC/l) 10. U/ 10. U/ 10. U/ 10. U/ 10. UI
Tetrachloroethene (UC/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. U/
1,1,Z,Z-Tetrachloroethane (UC/l) 5. U/ 5. U/ 5. U/ 5~ U/ 5. UI
Toluene (UC/l) -5. U/ 5. U/ 5. U/ 5. U/ 5- U/
Chlorobenzene (UC/l) 5. II/ 5. U/ 5. U/ 5. U/ 5. U/
Ethylbenzene (UC/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. U/
Styrene (UC/l) 5. UI 5. U/ 5. U/ 5. UI 5. III
Xyl enes (totol) (IIC/l) 5. U/ 5. U/ 5. U/ 5. II/ 5. U/
,""
Note: (1) Results are reported with qualifiers (loborotory QUlllifier/Oota Validation Qualifier) to the right 01 the volue.
-------
ANALYTICAL DATA REPORT "
Uoodstock landfill RIIFS
Uoodstock. Illinois
Hatrix: GU Type: vac
Parameter UK-GUT805-02 02/06191 UK-GUTB06-02 02/07/91 WK-GUTB08-02 02/11/91 UK-GUT810-02 0~/01/91 UK-GUJBII-OZ 0~/02/91
----...... -- --_.. ........... ......- ---.... --....... ---------------..-------- -----..-..-........-..---------- """"..---........... -----.. --.. --... ---------..-..--.....----..--.. .. .....- -..--.......... --...... -............
Chloromethane (UG/l) 10. UI 10. UI 10. UI 10. UI 10. tll
Bromomethane (UG/l) 10. tll 10. tll 10. tll 10. tll 10. tll
Vinyl chloride (tlG/l) 10. tll 10. tll 10. tll 10. UI 10. tll
Chloroethane (UG/l) 10. tll 10. UI 10. tll 10. UI 10. UI
Hethylene chloride (UG/l) 5. ul 5. UI 6. UI 5. UI 22. 8/t1
Acetone (UG/I) 10. UI 10. UI 9. JI 10. UI 10. tll
'Carbon dhulficfe tUG/l) 5. UI 5. UI 5. UI 5. UI 5. tll
1,l'Dlchloroethene (UG/l) 5. UI 5. UI 5. UI 5. UI 5. tll
1.1'0Ichloroethane (UG/I) 5. UI 5. UI 5. tll 5. UI 5. tll
1,2-Dlchloroethene (total) (UG/l) 5. tll 5. tll 5. UI 5. UI 5. UI
Chloroform (UG/I) 5. UI 5. UI 5. tll 5. UI 5. UI
1,2'0lchloroethane (UG/I) 5. UI 5. UI 5. UI 5. UI 5. tll
2-Butanone (UG/l) 10. UI 10. UI 10. UI 10. tll 10. UI
1,1,1-Trlchloroethane (UG/l) 5. tll 5. tll 5. UI 5. tll 5. tll
Carbon tetrachloride (tlG/l) 5. UI 5. UI 5. UI 5. UI 5. tll
Vinyl acetate (tlG/l) 10. tll 10. tll 10. tll 10. UI 10. tll
Bromodlchloromethane (UG/l) 5. UI 5. UI 5. UI 5. UI 5. tI/
1,2'Dlchloropropane (tlG/I) 5. U/ 5. U/ 5. UI 5. UI 5. U/
cls-1,3-0Ichloropropene (UG/I) 5. U/ 5. U/ 5. U/ 5. U/ 5. U/
Trlchloroethene (tlG/l) 5. UI 5. U/ 5. UI 5. UI 5. UI
Olbromochloromethane (UG/I) 5. tI/ 5. UI 5. tI/ 5. U/ 5. UI
1,1,2'Trlchloroethane (UG/l) 5. U/ 5. U/ 5~ U/ 5. U/ 5. UI
Benzene (UG/l) 5. U/ 5. UI 5. U/ 5. UI 5. UI
trans-I,3-0Ichloropropene (UG/l) 5. U/ 5. U/ 5. UI 5. U/ 5. UI
Bromoform (UG/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. UI
~'Hethyl-2'pentanone (UG/l) 10. UI 10. U/ 10. tll 10. tli 10. tll
2'Hexanone (UG/l) 10. UI 10. U/ 10. UI 10. U/ 10. UI
Tetrachloroethene (UG/l) 5. U/ 5. UI 5. U/ 5. tI/ 5. UI
1,I,2,2-Tetrachloroethane (UG/l) 5. UI 5. UI 5. UI 5. UI 5. UI
Toluene (UG/l) 5. U/ 5. U/ 5. UI 5,. U/ 5. III
Chlorobenzene (UG/l) 5. tll 5. UI 5. tll ,5. tll 5. tll
Ethylbenzene (UG/l) 5. UI 5. UI 5. UI 5. U/ 5. U/
Styrene (UG/I) 5. UI 5. UI 5. tll 5. tll 5. tll
Xylenes (total) (tlG/l) 5. tll 5. tI/ 5. UI 5. UI 5. UI
Note: (1) Results are reporled with qualifiers (l.ilhoratory Oualifier/Data Valicfation Ouollfler) to the right of the value.
, '.
. .
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, "
, ,
ANALYTICAL DATA REPORT
Uoodstock landfill Al/fS
Uoodstock, Illinois
Hatrix: GU Type: SVOC
Generated by: CAU
Date Issued: 10-HAY-91
Parameter
UK-GUlBOI-01 11/02/90
UK'GUfB02-01 11/02/90
UK-GUHUOID-OI 10/]1/90
UK-GUfBOI-01 10/]1/90
.....-..----....----..------------
.....-------------------
................................... .. .... ...........
------------------------
-------------..----------
UK-GUHUOIS-01 10/]1/90
-....--..--.. .--...- ---.. ----..-
Phenol (IIG/l) 10. III 10. III 10- III. 10. III 10. III
bls(2-Chloroethyl) ether (IIG/l) 10. III 10. UI 10. III 10. III 10. UI
2-Chlorophenol (UG/l) 10. UI 10. UI 10. III 10. UI 10. UI
1,3-Dlchlorobenzene (UG/l) 10. UI 10. UI 10. UI 10. UI 10. UI
1,'-Dlchlorobenzene (UG/l) 10. UI 10. UI 10. III 10. UI 10. III
Benzyl Alcohol (UG/l) 10. UI 10. UI 10. UI 10. UI 10. UI
1,2-Dlchlorobenzene (UG/l) 10. UI 10. UI 10. UI 10. UI 10. UI
2-Hethylphenol (UG/l) 10. UI 10. UI 10. UI 10. UI 10. UI
bls(2-Chlorolsopropyl)ether (UG/l) 10. UI 10. UI 10. UI 10. UI 10. UI
'-Hethylphenol (IIG/l) 10. UI 10. III 10. UI 10. UI 10. UI
N-Nltroso-di-n-dlpropylamlne (IIG/l) 10. UI 10. UI 10. UI 10. UI 10. III
Hexachloroethane (UG/l) 10. UI 10. UI 10. UI 10. UI 10. UI
Nitrobenzene (UG/l) 10. UI 10. UI 10. UI 10. UI 10. III
Isophorone (UG/l) 10. III 10. III 10. UI 10. UI 10. UI
2-Nltrophenol (UG/l) 10. UI 10. III 10. III 10. III 10. III
2,'-Olmethylphenol (IIG/l) 10. III 10. III 10. III 10. UI 10. III
Benzoic Acid (UG/l) 50. UI 50. III 50. III 50. III 50. III
bls(2-Chloroethoxy)methane (IIG/l) 10. III 10. III 10. III 10. III 10- III
2,'-Dlchlorophenol (IIG/l) 10. III 10. III 10. III 10. III 10. III
1,2.'.Trlchlorobenzene (UG/l) 10. III 10. III 10. III 10. UI 10. III
Naphthalene (UG/l) 10. UI 10. III 10. UI 10. UI 10. UI
'-Chloroanlline (UG/l) 10. UI 10. III 10. UI 10. III 10. III
Hexachlorobutadlene (IIG/l) 10. III 10. III 10. III 10. III 10. UI
'-Chloro.]-methylphenol (IIG/l) 10. UI 10. UI 10. UI 10. III 10. U/
2-Methylnaphthalene (UG/l) 10. UI 10. UI 10. .UI 10. UI 10. UI
Hexachlorocyclopentadlene (IIG/l) 10- UI 10. III 10. UI : 10. UI 10. UI
2,',6-Trlchlorophenol (IIG/l) 10. UI 10. III 10. UI 10. UI 10. UI
2,',5-Trlchlorophenol (UG/l) 50. UI 50. III 50. III 50. UI 50. UI
2-Chloronaphthalene (UG/l) 10. III 10. UI 10. UI 10. U/ 10. UI
2-Nltroanlline (UG/l) 50. UI 50. III 50. UI 50. UI 50. lI/
Dimethylphthalate (UG/l) 10. III 10. UI 10. III 10. UI 10. III
Acenaphthylene (IIG/l) 10. UI 10. III 10. UI 10.' III 10. UI
2,6-0inltrot~luene (IIG/l) 10. UI 10. III 10. III 10. UI 10. III
3-Nitroaniline (IIG/l) 50. 11/ 50. III 50. III 50. III 50. III
Acenaphthene (UG/l) 10. III 10. ,pi 10. UI 10. III 10. III
2,t.'Oinhrophenol (IIG/U 50. III 50. il, 50. UI 50. UI 50. III
t,'Nitrophenol (IIG/l) 50. III 50. III 50. III 50. III 50. III
Note: (1) Results are reported \lith qualifiers (lnl~ratory Qualifler/Oata Validation Ouallfler) to the right of the value.
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ANALYTICAL DATA REPORT 2
Uoodstock Landfill RI/FS
Uoodstock, illinois
Hatrlle: GU Type: SVOC
Parlmeter UK-CUHU020-01 10/31/90 UK-GUHU02S-01 10/31/90 UK-GUHU02S-91 10/31/90 UK-GUHU03D-01 11/01/90 UK-GUHUOJS-OI 11/01/90
.....--.........-- ...... -....... --.... --.......... --... ------------------------ ---------------...-------.. ----------------..-..----- .......... -.. ...-.. -.... -.. -.....- .......... ... ---............ --"........... ..... ---..
Phenol (UG/L) 10. UI 20. UI 10. UI 10. UI 10. UI
bll(2'Chloroethyl) ether (UC/L) 10. UI 20. UI 10. UI 10. U/ 10- III
2'Chlorophenol (UG/L) 10. UI 20. UI 10. II/ 10. UI 10. IJI
1,3-0Ichlorobenrene (IIG/L) 10. UI 20. UI 10. UI 10. U/ 10. III
1,4-Dlchlorobenzene (UG/L) 10. U/ 20. UI 10. III 10. U/ 10. II/
Benzyl Alcohol (UC/L) 10. U/ 20. U/ 10. II/ 10. UI 10. II/
1,2-Dlchlorobenzene (UG/l) 10. UI 20. UI 10. III 10. UI 10. UI
2-Hethylphenol (UG/L) 10. UI 20. UI 10. III 10. III 10. III
bls(2'Chlorolsopropyl)ether (IIC/L) 10. 1/1 20. III 10. II/ 10. III 10. U/
4'Hethylphenol (UG/L) 10. III 20. III 10. U/ 10. III 10. U/
N-Nltroso-dl'n-dipropylnmine (UG/L) 10. U/ 20. UI 10. U/ 10. II/ 10. III
Helllchioroethane (IIG/L) 10. III 20. III 10. III 10. III 10. III
Nitrobenzene (UG/l) 10. UI 20. III 10. ul 10. UI 10. u/
I.ophorone (UC/L) 10. II/ 20. U/ 10. III 10. UI 10. U/
2'Nltrophenol (UG/L) 10. u/ 20. UI 10. U/ 10. UI 10. U/
2,4-0Imethylphenol (UG/l) 10. U/ 20. UI 10. III 10. UI 10. III
Benzoic Acid (UG/L) 50. UI 100. UI 50. UI 50. III 50. u/
bll(2'Chloroethoxy)methane (IIG/L) 10. III 20. UI 10. III 10. UI 10. UI
2,4-Dlchlorophenol (UG/L) 10. UI 20. UI 10. III 10. III 10. UI
1,2.4-Trlchlorobenzene (IIG/L) 10. UI 20. III 10. UI 10. III 10. UI
Naphthalene (IIG/L) 10. UI 20. III 10. u/ 10. u/ 10. UI
4-Chloroanlline (UG/l) 10. U/ 20. UI 10. UI 10. U/ 10. U/
Hexachlorobutadlene (UG/l) 10. UI 20. UI 10. U/ 10. UI 10. U/
4'Chloro']'rnethylphenol (UG/L) 10. UI 20. U/ 10. U/ 10. U/ 10. U/
2-Hethylnaphthalene (UG/L) 10. III 20. U/ 10. II/ 10. III 10. UI
Hexachlorocyclopentadlene (IIG/L) 10. UI 20. UI 10. III 10. II/ 10. U/
2,4.6-Jrlchlorophenol (IIG/L) 10. UI 20. UI 10. III 10. III 10. U/
2.4,5-Trlchlorophenol (IIG/L) 50. U/ 100. III 50. II/ 50. II/ 50. III
2-Chloronaphthalene (IIG/L) 10. UI 20. III 10. III 10. III 10. UI
2'Nltroanlllne (UG/L) 50. U/ 100. III 50. UI 50. UI 50. III
Olmethylphthalate (IIG/L) 10. UI 20. U/ 10. UI 10. III 10. II/
Acenaphthylene (UG/L) 10. III 20. III 10. III 10. II/ 10. UI
2,6-Dinltrotoluene (UG/l) 10. III 20. UI 10. III 10. UI 10. U/
3-Nitroanlline (UG/l) 50. III 100. UI 50. UI 50. II/ 50. II/
Acenaphthene (UG/l) 10. III 20. III 10. UI 10. III 10. II/
2,4'0Inltrophenol (UG/l) 50. lI/ 100. U/ 50. III 50. U/ 50. II/
"Nltrophenol (IIG/l) 50. II/ 100. II/ 50. U/ 50. UI 50. u/
Nole; (I) Results ore reported with quol ifiers (lllborlltory Quallfier/Oata Validation QUllllfier) to the right of the value.
, '.
. ,
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I,::'
." :::
ANALYTICAL DATA REPORT J
Uoodstock landfill Rl/fS
Uoodstock. Illinois
HUr I x: GII Type: SVOC
Paremeter UK'GIIHII04D.01 11/01/90 UK'GUMII04s.01 11/01/90 UK-GIIHII05D-01 11/01/90 UK-CIIHU05D-91 11/01/90 \/"-CUMII055-01 11/01/90
.............. .................... ........ --......-. ---....-.. ..............-...... -.---......-.........----.....- ..--....--...... "-......-........--.. ...................---..----........ "............--....-...................
Phenol (UC/l) 10. UI 10. UI 10. UI 10. UI 10. UI
bls(Z'Chloroethyl) ether (UG/l) 10. UI 10. UI 10. UI 10. UI 10. III
2'Chlorophenol (UG/L) 10. UI 10. UI 10. UI 10. UI 10. III
1.3-Dichlorobenzene (UG/l) 10. UI 10. UI 10. UI 10. UI 10. UI
I,~-Dlchlorobenzene (UC/l) 10. UI 10. UI 10. UI 10. UI 10. III
Benzyl Alcohol (UG/l) 10. UI 10. UI 10. UI 10. III 10. III
1,Z'Dlchlorobenzene (UG/L) 10. UI 10. III 10. UI 10. UI 10. III
2'Hethylphenol (IIG/l) 10. III 10. III 10. U/ 10. UI 10. III
bls(2-Chlorolsopropyl)ether (UG/l) 10. UI 10. III 10. UI 10. UI '0. UI
~'Hethylphenol (IIG/l) '0. III 10. III 10. UI 10. UI 10. UI
N'Nltroso-dl'n-dipropylamine (UG/L) 10. UI 10. III 10. III 10. III '0. III
Hexachloroethane (IIC/l) 10. III 10. III 10. III 10. UI 10. UI
Nitrobenzene (IIG/l) 10. III 10. UI '0. UI 10. UI '0. U/
Isophorone (UG/l) 10. UI 10. III 10. UI '0. UI 10. U/
2'N I trophenol (UG/l) 10. UI 10. III 10. II/ 10. III 10. III
2.~'Dlmethylphenol (IIG/l) 10. III 10. III 10. III 10. III '0. III
Benzoic AcId (IIG/l) 50. UI 50. III 50. UI 50. UI 50. U/
bls(2'Chloroethoxy)methane (UG/l) 10. UI 10. III to. III 10. III 10. III
2,~'Dlchlorophenol (IIG/l) 10. UI 10. III 10. III 'O. III 10. III
1,2.~'Trlchlorobenzene (UG/l) 10. III 10. III 10. III 10. III 10. III
Naphthalene (IIG/l) 10. III 10. UI 10. III' '0. III '0. III
4.thloroanlllne (UG/l) 10. III 10. III 10. UI 10. UI '0. II/
Hexachlorobutadlene (UG/L) 10. UI 10. UI 10. UI 10. UI 10. UI
4'Chloro-3.methylphenol (UG/l) 10. UI 10. UI 10. III 10. UI 10. UI
2'Hethylnaphthalene (IIG/l) 10. UI 10. III 10. UI 10. UI 10. III
Hexachlorocyclopentadlene (UG/l) 10. UI 10. UI 10. III 10. UI 10. III
2,4,6'Trlchlorophenol (IIG/l) 10. III 10. UI 10. III 10. III 10. UI
2,4,5'Trlchlorophenol (IIG/L) 50. III 50. III 50. III 50. III 50. III
2'Chloronaphthalene (IIG/l) '0. III 10. III 10. III 10. UI 10. U/
2'Nitroanlline (UG/l) 50. UI 50. III 50. III So. III 50. III
Dlmethylphthalate (UG/l) 10. III 10. III 10. UI 10. III 10. UI
Acenaphthylene (IIG/l) '0. III 10. III 10. III 10. UI 10. UI
2.6'Olnltrotoluene (IIG/l) 10. III 10. III 10. III 10. III '0. UI
3-Nltroaniline (IIC/l) 50. III 50. III 50. III 50. III 50. III
Acenaphthene (UC/l) 10. UI 10. III 10. III 10.. III 10. III
2.4'0Inltrophenol (IIG/L) 50. III 50. II/ 50. III 50. U/ 50. U/
4-NI trophenol (IIG/l) 50. II/ 50. III 50. III 50. III 50. III
".
,I;
Note: (1) Results 8re reported with qualifiers (l.nhoratory Oual i f ier/Oata Val idatlon Ouall fler) to the right 0' the value.
-------
ANALYTICAL DATA REPORT I,
lIoodstock landf It I Rl/fS
lIoodstock, Illinois
Matrix: GII Type: SVOC
Parameter IIK-GUMU06D-01 11/02/90 IIK-GUHII06S-01 11/02/90
---------.-------------------- ------------------------ -------------.---.--....
Phenol WG/l) 10. U/ 10. U/
bll(2-Chloroethyl) ether (UG/l) 10. U/ 10. U/
2-Chlorophenol (UG/l) 10. U/ 10. U/
1,3-0lchlorobenzene (UG/L) 10. U/ 10. U/
1,'-Olchlorobenzene (UG/l) 10. U/ 10. U/
Benzyl Alcohol (UG/l) 10. U/ 10. U/
1,2-Dlchlorobenzene (UG/l) 10. U/ 10. U/
2-Hethylphenol (UG/l) 10. U/ 10. U/
btl(2'Chlorolsopropyl)ether (UG/l) 10. U/ 10. U/
'-Hethylphenol (UG/l) 10. U/ 10. U/
N-Nltroso-dl'n-dlpropylamlne (UG/L) 10. U/ 10. U/
Hexachloroethane (UG/L) 10. U/ 10, U/
Nltrobenrene (UG/l) 10. U/ 10. U/
'Iophorone (UG/l) 10. U/ 10. U/
2-Nltrophenol (UG/L) 10. U/ 10. U/
2,'-Olmethylphenol (UG/l) 10. U/ 10. U/
Benzoic Acid (UG/l) 50. U/ 50. U/
bll(2-Chloroethoxy)methane WG/l) 10. UI 10. U/
2,4-0lchlorophenol (UG/l) 10. U/ 10. UI
1,2,4-Trtchlorobenzene (UG/L) 10. U/ 10. U/
Naphthalene (UG/l) 10. U/ 10. U/
4-Chloroanlllne (UG/l) 10. U/ 10. U/
Hexachlorobutadlene (UG/L) 10. U/ 10. U/
4-Chloro-3'methylphenol (UG/l) 10. U/ 10. U/
2'Hethylnephthotene (UG/l) 10. UI 10. U/
Hex8chlorocyclopentadlene (UG/l) 10. u/ 10. U/
2,4,6-Trtchlorophenol (UG/l) 10. U/ 10. UI
2,4,5-Trlchlorophenol (UG/l) 50. U/ 50. U/
2'Chloronaphtholene (UG/l) 10. U/ 10. U/
2-Nltroenlline (UG/l) 50. U/ 50. UI
Olmethylphthelote (UG/L) 10- U/ 10. U/
Acenaphthylene (UG/l) 10. U/ 10. U/
2,6-Dlnltrotoluene (UG/L) 10. U/ 10. U/
3-Nltroenlllne (UG/L) 50. U/ 50. u/
Acenaphthene (UG/l) 10. UI 10. U/
2,4'Olnitrophenol (UG/l) 50. u/ 50. U/
4-Nltrophenol (UG/l) 50. ul 50. U/
Note: (1) Results are reported with qualifiers (lnhoratory Qualifier/Data Validation Qualifier) to the right of the value.
. '.
" ,
-------
, "
J; ,.
ANALYTICAL DATA REPORT 5
Uoodstock landfill Rl/fS
Uoodstock. tllinol s
Hatrlx: GU Type: SVOC
Parameter UK-GUBUOI-01 11/02/90 UK-CUfBOI-01 10/31/90 UK-CUfB02-01 11/02/90 YK-GUHUOI0-01 10/31/90 UK-GUHUOIS-01 10/]1/90
.-.... -.... ......................................-.... .-....-_.. ...- ....-......------- -------..---------------. -..------......-----......--.- ..- ---.. --......-........ ---.......... ........ .... ...... .... .. .. .. .. ...... ....... .. .. ..
Dlbenzo'uran (UC/l) '0. UI '0. UI 10. UI 10. UI 10. III
2.4'Dlnitrotoluene (UG/l) '0. UI '0. UI '0. UI 10. UI 10. UI
Dlethylphthalnte (UC/l) 10. UI '0. UI 10. UI 10. UI 10. UI
4-Chlorophenyl-phenylether (UC/l) to. UI 10. UI 10. UI 10. UI 10. UI
fluorene (UG/l) 10. UI 10. U/ 10. U/ 10. UI 10. UI
4'Nltroanillne (UC/l) 50. UI 50. UI 50. UI 50. U/ 50. UI
4.6-Dinitro-2-methylphenol (UC/l) 50. UI 50. U/ 50. UI 50. U/ 50. UI
N'nltrosodlphenylamlne (UG/l) 10. UI 10. U/ 10. UI '0. U/ 10. UI
4'Bromophenyl-phenylether (UC/l) 10. UI 10. U/ 10. U/ 10. UI 10. UI
Hexachlorobenzene (UC/l) 10. UI 10. UI 10. UI 10. UI 10. III
Pentachlorophenol (UG/l) 50. UI 50. UI 50. UI 50. U/ 50. III
Phenanthrene (UC/l) to. UI 10. U/ 10. U/ 10. U/ 10. UI
Anthracene (UC/l) 10. U/ 10. U/ to. UI 10. UI 10. UI
DI-n-butylphthalate (UC/L> 10. U/ '0. UI 10. UI 10. UI 10. UI
fluoranthene (UC/l) 10. U/ 10. U/ 10. UI 10. UI 10. UI
Pyrene (UC/l) 10. UI 10. UI 10. UI 10. UI 10. UI
Butylbenzylphthalate (UC/l) 10. UI 10. UI 10. UI 10. UI 10. UI
3.3"Dlchlorobenzldine (UG/l) 20. UI 20. UI 20. UI 20. UI 20. UI
8enzo(a)anthracene (UC/l) 10. U/ 10. U/ 10. UI 10. U/ 10. U/
Chrysene (UC/l) 10. U/ 10. U/ 10. U/ 10. U/ 10. UI
bll(2-ethylhexyl)phthalate (UC/l) 10. U/ 10. UI 10. UI 10. UI 10. UI
DI'n-octyl Phthalate (UG/l) 10. UI 'o. UI 10. UI 10. UI 10. UI
8enzo(b)fluoranthene (UC/L) 10. UI 10. UI 10. UI 10. UI 10. UI
8enzo(k)'luoranthene (UG/l) 10. UI 10. U/ 10. U/ 10. UI 10. UI
Benro(a)pyrene (UC/l) 10. U/ 10. U/ 10. U/ 10. U/ 10. UI
Indeno(1.2.3-cd)pyrene (UG/l) 10. UI 10. U/ 10. U/ 10. U/ 10. UI
Dlbenz(a.h)anthracene (IIG/l) 10. UI 10. U/ 10. U/ 10. U/ 10. UI
Benro(g.h.l)perylene (UG/l) 10. U/ 10. U/ 10. UI 10. UI 10. UI
.j'
Note: (I) Results nre rcported with qual itiers (l.aboratory Quallfier/Data Validation QualifIer) to the right o' the value.
-------
ANALYTICAL DATA REPORT 6
Uoodstock landfill Rl/fS
Uoodstock, Illinois
HatriK: GII Type: SVOC
Perameter UK-GYHIIOZO'01 10/31/90 UK-GUHII02S'01 10/31/90 UK-GUHIIOZS-91 10/31/90 UK-GUHU030-01 11/01/90 UK-GUHUO]S-01 11/01/90
........................ -......-................ ..... .................. ....-................-- ......-........---..-..--------- --------..-..------ - -- .-..--------------.......-..- .... ................ .. .. ...... .............. ....
Olbenzo'uran (IIG/l) 10- III 20. UI 10- UI 10. UI 10. III
2,4-0Inltrotoluene (UG/l) 10. III 20. III 10. III 10. II/ 10. III
Diethylphthalate (IIG/l) 10. UI 20. II/ 10- U/ 10. III 10. III
4-Chlorophenyl-phenylether (IIG/l) 10. III 20. UI 10. UI 10. UI 10. III
Fluorene (IIG/l) 10. U/ 20. II/ 10. III 10. III 10. III
4-Nltroanlline (IIG/l) 50. UI 100. U/ 50. UI 50. III 50. III
',6-Dlnltro'2-methylphenol (IIG/l) 50. II/ 100. III 50. III 50. III 50. III
N-nltrosodlphenylamlne (IIG/l) 10. III 20. III 10- III 10- III 10. III
'-'romophenyl-phenylether (IIG/l) 10. U/ 20. III 10. II/ 10. II/ 10. III
Hexaehlorobenzene (IIG/l) 10. UI ?O. II/ 10. II/ 10. U/ 10. UI
Pentachl orophenol (IIG/l) 50. II/ 100. II/ 50. II/ 50. III 50- III
Phenanthrene (IIG/l) 10. III 20. III 10. III 10. III 10. III
Anthracene (IIG/l) 10. II/ 20. III 10. II/ 10. II/ 10. III
DI-n'butylphthalate (UG/l) 10. II/ 20. II/ 10. II/ 10. II/ 10- III
fluoranthene (IIG/l) 10- II/ 20. II/ 10. II/ 10. . UI 10. III
Pyrene (IIG/l) 10. UI 20. II/ 10. III 10. II/ 10. UI
Butylbenzylphth81ate (IIG/l) 10. II/ 20. II/ 10. III 10. II/ 10. II/
3,3"Dlehlorobenzldine (IIG/l) 20. II/ 40. II/ 20. III 20. U/ 20- III
Benlo(8)8nthr8cene (IIG/l) 10. III 20. II/ 10. III 10. II/ 10. III
Chrysene (IIG/l) 10. II/ 20. III 10. II/ 10. III 10. III
bls(2-ethylheKyl)phthalate (IIG/l) 10. II/ 20. III 10. III 10. II/ 10. II/
DI-n-oetyl Phthalate (IIG/l) 10. II/ 20. III 10. II/ 10. U/ 10. III
BenIO(b)fluor8nthene (UG/l) 10- III 20. III 10. II/ 10. UI 10. III
Benlo(k)'luor8nthene (UG/l) 10. II/ 20. III 10. III 10. UI 10. UI
Benlo(a)pyrene (IIG/l) 10. III 20. UI 10. UI 10. U/ 10. UI
Indeno(1,2,3-cd)pyrene (UG/l) 10. II/ 20. III 10. U/ 10. III 10. U/
Dlbenl(8,h)8nthr8cene (IIG/l) 10. II/ 20. III 10. III 10. UI 10- III
Benlo(g,h,I)perylene (IIG/l) 10. III 20. III 10. II/ 10. UI 10. UI
Note: (I) Results ore reported with qunli'iers (laborntory Ouollfier/Data Validation Qualifier) to the right of the value.
, '.
It f.
-------
, "
I ~ ~
ANALYTICAL DATA REPORT 7
~oodstock landfill R I/rS
Uoodstock. 1IIInol5
Hatrlll: G\I Tvpe: SVOC
Par-ter UK-G~\l040-01 11/01/90 UK-GUHU04S-01 11/01/90 UK-GUHU050.01 11/01/90 UK-G~\l05D-91 11/01/90 UK-GUHU05S-01 11/01/90
....................... .... .................. .... .. -... ........ .e.._--.....-" - -.. --------..-... ..----......------------.--- -..--.-..---..--------........-. ......... .......................... .............. .. ........ .... .... .. .. .. .. .. .. .. ... .... ...... .. - ..
Dlbenrofuran (UG/l) '0. UI 10. UI '0. UI '0. UI '0. III
2.4-Dlnltrotoluene (UG/l) 10. UI 10- UI '0. UI 10. UI '0. III
Dlethylphthalate (UG/l) 10. UI '0. UI '0. UI '0. UI '0. UI
4-Chlorophenyl-phenylether (UG/l) 10. UI '0. UI 10. UI 10. UI 10. III
fluorene (UG/l) 10. UI 10. UI 10. UI 10. UI 10. UI
4-Nltroanlllne (UG/l) 50. UI 50. UI 50. UI 50. UI 50. UI
4,6-0Inltro-2-methylphenol (UG/l) 50. UI 50. UI 50. UI 50. Uf 50. III
N'nltrosodlphenylamlne (UG/l) '0. UI 10. UI 10. UI '0. UI 10. UI
4'Bromophenvl'phenvlether (UG/l) '0. UI 10. UI 10. UI 10. UI '0. UI
HeKachiorobenzene (UG/l) '0. UI '0. UI '0. UI '0. UI '0. UI
Pentachlorophenol (UC/l) 50. UI 50. UI 50. UI 50. UI 50. UI
Phenanthrene (UC/l) 10. UI 10. UI 10. UI 10. UI 10. UI
Anthracene (UG/l) 10. UI 10. UI '0. UI '0. UI '0. UI
DI-n-butvlphthalate (UG/l) '0. UI '0. UI '0. UI '0. UI '0. UI
fluoranthene (UC/l) '0. ul '0. UI 'O. ul '0. UI 10. UI
Pyrene (UC/l) 10. UI 10. UI '0. UI 10. UI 10. UI
8utylbenrylphthalate (UC/l) 10. UI 10. UI 10. III '0. UI 10. III
3,3"Dlchlorobenzldine (UG/l) 20. U/ 20. III 20. UI 20. U/ 20. III
8enlo(a)anthracene (UC/l) '0. UI '0. III '0. UI 10. III 10. III
Chrysene (UG/l) 10. II/ '0. II/ '0. II/ '0. III 10. III
bls(2.ethylheKyl)phthalate (UG/l) '0. UI 10. U/ 10. UI 10. UI 5. JI
Ol-n-octyl Phthalate (UG/l) 'O. UI '0. III '0. III 10. III '0. III
8enlo(b)fluoranthene (UC/l) 10. UI '0. U/ '0. III 'O. UI 10. UI
Benro(k)fluoranthene (UC/l) '0. UI 10. U/ '0. U/ '0. III '0. III
Benlo(a)pyrene (UG/l) 10. UI . 10. UI 10. UI '0. UI 10. UI
Indeno(1,2.3-cd)pyrene (UG/l) 10. U/ 10. U/ 10. U/ '0. U/ 10. U/
Dlbenr(e,h)anthrecene (UG/l) 10. U/. 10. U/ 10. U/ 10. UI 10. UI
Benro(9.h.l)perylene (UG/l) 10. UI 10. U/ 10. UI 10. U/ '0. UI
Note: (1) Results ere reported ..ith '1"el ilie,'s (lehoratory Qualifier/Data Validation Qualifier) to the right 01 the volue.
-------
ANALYTICAL DATA REPORT 8
Uoodstock landfill RI/FS
Uoodstock, illinois
Matrix: CU Type: SVOC
Puameter UK'CUHY060.01 11/02/90 UK-C~U06S'01 11/02/90
---............. -....... --- .......... -.. -.. ."""....--.... -"""".............--- --.......--.-....-....---..----
Oibenlofuran (UC/l) 10. U/ 10. U/
2,4-01nl trotoluene (IIC/l) 10. U/ 10- U/
Olethylphthalate (UC/l) 10. II/ 10. II/
'-Chtorophenyl-phenylether (UC/l) 10. U/ 10. II/
Fluorene (UC/l) 10. U/ 10. U/
'-Nltroanlllne (UC/l) 50. U/ 50. III
4,6'Olnltro-2'methylphenot (UC/l) 50. U/ 50. II/
N-nltrosodlphenylamine (UC/l) 10- U/ 10. U/
'-Bromophenyl-phenylether (UC/l) 10. U/ 10. U/
Hexachlorobenlene (UC/l) 10. U/ 10. II/
Pent8chlorophenol (UC/l) 50. II/ 50. U/
Phen8nthrene (IIC/l) 10. II/ 10. U/
Anthr8cene (UC/l) 10. II/ 10. UI
Ol'n-butylphthalate (UC/l) 10. U/ 10. U/
fluor8nthene (IIG/l) 10. II/ 10. U/
Pyrene (UC/l) 10. II/ 10. U/
Butylbenlytphthal8te (UC/l) 10. II/ 10. U/
3,3'-Olchlorobenlldlne (UC/l) 20. III 20. U/
Benlo(a)8nthracene (UC/l) 10. II/ 10. U/
Chrysene (UG/l) 10. II/ 10. UI
bls(2-ethylhexyl)phthalate (UC/L) 10. U/ 10. UI
ol-n-octyl Phth818te (UC/l) 10. UI 10. III
Benzo(b)fluorenthene (UC/L) 10. UI 10. III
Benlo(k)fluoranthene (UC/l) 10. U/ 10. II/
Benlo(8)pyrene (UC/l) 10. II/ 10. II/
Indeno(1,2,3-cd)pyrene (UC/l) to. II/ 10. II/
Dlbenl(8,h)anthr8cene (IIC/l) 10. II/ 10. U/
Benlo(g,h,l)perylene (UC/l) 10. U/ 10. U/
Note: (1) Results ore reported \lith quolifiers (I.nhoratory Qualifier/Data Validotlon Qualifier) to the right of the value.
, '.
, . 0
-------
"at~ix: t:...
Ce~era:~ :y: C~~
Cate Iss~~: Oi-CCT-91
"1:-C;"~W' 1-9'
08/08/91
(TVCA) Tentatively.ldentifi~ Volatiles
Comcovnd (Units)
s:.;)o!~"~r
- .
OF T;~TAT:v;~r IO~Tlr!E~
.coCs::c~ La~f;ll RI/FS
lOooCs:ocl:. Illinois
C::nc:entration
C::Jo\PCl;IiOS
LO/DVO
-------------------------------------------
19.
--...-----------...----...-----.
J/
Unknown (UCi/L)
.' ,". ...... ,'. ..
.
". .. '.. " " .
-------
Matrix: GW
Generated by: CAW
Cate Issued: 10-MAY-91
SUMMARY OF TENTATIVELY IDENTIFIED COMPOuNDS
Woodstock Landfill RI/FS
WOOdstock, Illinois
WIC-CiIlMW01S-01
10/31/90
(TVOA) Tentative{y-Identified Volatiles
Compound (Units)
Concent rat i on
LQ/DVQ
---.-.----..-------------------------------
---.-.--------------------------
ETHANE, 1, 1'-OXYBIS (UG/L)
7.
J/
WIC' CillMW01 S-02
02/06/91
(TVOA) Tentatively-Identified Volatiles
Compound (Units)
Concentration
LQ/DVQ
-------------------.------------.--.-----..
------.-------------------------
Unknown (UCi/L)
8.
J/JN
1/1( -CiIlM'olO2S-01
10/31/90
CTBNA) Tentativel y-Identi fi ed Semi -Volatiles
Compound (Units)
Concentrat i on
LQ/DW
-------------------------------------------
--------------------------------
Unknown (UG/L)
32.
J/
1/1( - CiIIM'olO7 - 0 1
02/06/91
(TVOA) Tentatively-Identified Volatiles
Compound (Units)
Concentration
LQ/DVQ
----------.-----------------------------.-.
-.-.----------------------------
Unknown (UG/L)
8.
J/JN
WIC-CiIlMW07-02
04/02/91
(TVOA) Tentatively-Identified Volatiles
Compound (Units)
Concentration
LQ/DVQ
.-----------------.---------------------.-.
----------------------------....
Unknown (UG/L)
6.
J/
:'
-------
, "
I: I
Matrix: S8 Type: SLINO
Generated by: CAU
Date Issued: 10-MAY-91
Parameter
.. -.-....... -.o...... ..-.................. -.. -....--
Total Organic Carbon (MG/KG)
Cation Exchange Capacity (MEO/L)
ANALYTICAL DATA REPORT
Uoodstoclt Landfill RifFS
Uoodstock, Illinois
WK-SBHUOI0-08.5 07/27/90 YK-S8HWOI0-41 07/30/90
YK-SBHY02-43 08/03/90
16000.
O.
.....-.................------..--
>/
U/
--..........----------.....----
-....-.........----..-...........-.... ..
>/
U/
16000.
O.
>/
/
YK-SBH~2-60 08/03/90
16000.
O.
-------.......----..-..-..-......
YK-S8HWO]-06 08/06/90
Note: (1) Results are reported with "u..lifiers (laboratory Qualifier/Data Validation Qualifier) to the right of the value.
16000.
3.95
>/
U/
16000.
o.
..-..-----........ ............ """""
>/
U/
-------
Hatrlx: SB
Type: SliND
ANALYTICAL DATA REPORT
Uoodstock Landfill Rl/fS
Uoodstock, Illinois
2
Parameter
UK-SBHU04-13.5 08/10/90
UK-SBHU05-22 08/01/90
ur-SBHU06-08.5 07/31/90
UK-SBHU06-33.5 07/31/90
---....-------------------.-...---
------------------------
------------------------
--..---... -...... -... -...... -... --.
...---.... ----..................... ---........
Total Organic Carbon (HG/KG)
Cation Exchange Capacity (HEQ/L)
16000.
O.
>1
U/
16000.
5.88
>1
1
140.
O.
1
UI
16000.
O.
>1
UI
Note: (1) Results are reported \lith qUAlifiers (laboratory Qualifier/Data Validation Qualifier) 10 Ihe right 01 the value-
, '.
,. ,
-------
DISQUALIFIED MONITORING WEll.. SAMPLES
..
':
-------
-.
d
...
-
I'OTE FOR APPE1'."DTX F-3a
A sampling error was made at four deep monitoring wells i:1 the Phase I, Round 1 sampiing
(October 31 to November 2,1991). The analytical results which were disqualifie.d 2.S a
result of the sampling error are presented in this Appendix. .
The initial analytical results (from October 31 to November 2, 1991 sampling) indicated
that trichloroethylene (TCE) and Xylenes had been detected at or below detection limit in
monitoring wells M\V-1D, MW -2D, MW -5D, and MW -6D; total xylenes were also
estimated at 2 u!1:/1 at each of these wells. Durin2 data validation, it was discovere.d the.:
trace levels of TCE were also found in the field blanks collected through the bladder pump
which had been used to purge and sample these wells. The blanks indicated TCE leve\s of
18 ug/l and a xylene level of 2 ug/l. It was discovered that the pump used to purge these
wells had previously been used at a site contaminated with TCE. These monitoring wells
were re-sampled on December 12, 1990. The results of the resampling indicated no
detection of either trichloroethylene or xylenes.
-------
. .'
I: 0;:
ANALYTICAL DATA REPORT
Voodstock landfill Rl/fS
Voodstock, Illinois
Hatrlx: GV Type: VOA
Generated by: CAV
Date Issued: 04-JUN'91
Parameter ~-GWHUOID'BAD 10/31/90 VK-G~02D'BAD 10/31/90 VK . GI.tIW5D' 9BAD 11/01/90 UK-GUHU05D-BAD 11/01/90 VK-GUHU060-BAD 11/02/90
...-.- ........................ ........................... ................... ..... -................ ............--....................-..-..- ..........---..---..-......-..-..-- .... --...---....-............................ ---......-....-...-..""""" --""'''''
Chloromethane (UG/l) 10. u/ 10. U/ 10. U/ 10. U/ 10. U/
Bromomethftne (UG/l) 10. U/ 10. U/ 10. U/ 10. U/ 10. U/
Vinyl chloride (UG/l) 10. U/ 10. U/ to. U/ 10. U/ 10. lI/
Chloroethane (UG/l) 10. U/ to. lI/ to. u/ to. U/ 10. u/
Hethylene chloride (UG/l) 5. lI/ 5. U/ 5. lI/ 5. lI/ 5. U/lIJ
Acetone (UG/l) 10. U/ 10. U/ to. U/ 10. U/ to. U/
Carbon disulfide (UG/l) 5. U/ 5. lI/ 5. U/ 5. lI/ 5. U/
l,t'Dlchloroethene (UG/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. lI/
1,l'Dlchloroethftne (UG/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. U/
t,Z-Dlchloroethene (total) (UG/l) 5. U/ 5. UI 5. U/ 5. U/ 5. U/
Chloroform (UG/l) 5. U/ 5. UI 5. U/ 5. U/ 5. U/
1,2'Dlchloroethane (lIG/l) 5. lI/ 5. UI 5. U/ 5. III 5. U/
Z'Butanone (UG/l) to. U/ 10. U/ to. U/ 10. U/ 10. U/
l,t,l'Trlchloroethane (UG/l) 5. U/ 5. UI 5. U/ 5. U/ 5. U/
Carbon tetrachloride (UG/l) 5. UI 5. UI 5. U/ 5. UI 5. U/
Vinyl acetate (UG/l) to. UI 10. UI to. u/ 10. U/ 10. U/
Bromodlchloromethane (UG/l) 5. UI 5. UI 5. U/ 5. U/ 5. U/
1,2'Dlchloropropane (UG/l) 5. U/ 5. UI 5. . U/ 5. U/ 5. U/
cls-I,3-Dlchloropropene (UG/l) 5. U/ 5. UI 5. U/ 5. UI 5. U/
Trlchloroethene (UG(l) 5. 'll 10. JIll 4. J/ll 4. J/U 4. J/
Dlbromochloromethane (UG/l) 5. UI 5. UI 5. UI 5. UI 5. UI
1,I,Z-Trlchloroethane (UG/l) 5. UI 5. UI 5. U/ 5. UI 5. UI
Benzene (UC/l) 5. UI 5. UI 5. UI 5. U/ 5. U/
trens-I,3-0Ichloropropene (UG/l) 5. U/ 5. UI 5. UI 5. U/ 5. UI
Bromoform (UG/l) 5. UI 5. UI 5. UI 5. UI 5. UI
4'Hethyl-2-pentenone (UG/l) 10. UI 10. UI 10. UI 10. UI 10. III
2-HeKanone (lIG/l) 10. III to. UI 10. lI/ 10. UI 10. u/
Tetrachloroethene (UG/l) 5. UI 5. UI 5. UI 5. UI 5. UI
l,t,2.2'Tetrachloroethane (UG/l) 5. u/ 5. UI 5. UI 5. UI 5. U/
Toluene (UG/l) 5. U/ 5. UI 5. U/ 5. UI 5. U/
Chlorobenzene (UG/l) 5. U/ 5. UI 5. UI 5. lI/ 5. U/
Ethylbenzene (UG/l) 5. U/ 5. UI 5. lI/ 5. UI 5. II/
Styrene (UG/L> 5. III 5. UI 5. UI 5. UI 5. UI
Xylenes (total) (UG/l) 2. J/ll 1. J/U 2. J/U 2. J/U 2. J/
Note: (1) Results are reportee! with qualifiers (laboratory Qualifler/Data Validation Qualifier) to the right of the value.
-------
Matrix: GU Type: VOA
Generated by: CAU
Date Issued: 04-JUN-91
POSITIVE DETECT/USABlE ANALYTICAL DATA REPORT
Uaodstack landfill RI/FS
Uoodstock, Illinois
Parameter
WK-GWHW01D-DAD 10/31/90
WK-GUHW02D-BAD 10/31/90
WK-GUHU05D-9DAD 11/01/90 UK-GUHU05D-DAD 11/01/90
--_e_...... .......... -..... --.... --........ --..
..........---------..-...........
--------------------...---
....--..-..----........--------
.. -.......... -.. --.....-....... -- --........
Chloromethane (UG/l)
Bromomethane (UG/l)
Vinyl chloride (UG/l)
Chloroethane (UG/l)
Methylene chloride (UG/l)
Acetone (UG/l)
Cerban disulfide (UG/l)
1,1-0Ichloroethene (Ue/l)
1,1-0Ichloroethane (UG/l)
1,Z-Dlchloroethene (total) (\JG/l)
Chloroform (Ue/l)
1,2-0Ichloroethane (Ue/l)
2-Sutanone (Ue/l)
1,1,1-Trlchloroethane (UG/l)
Carbon tetrachloride (UG/l)
Vinyl acetete (UG/l)
Bromodlchloromethane (UG/l)
1,Z-Dlchloropropane (UG/l)
cls-1,3'Olchloropropene (Ue/l)
Trlchloroethene (UG/l)
Dlbromochloromethene (UG/l)
1,1,2-Trlchloroethane (UG/l)
Benzene (UG/l)
trens-1,3-Dlchloropropene (UG/l)
Bromoform (UG/l)
4-Hethyl-2-pentanone (UG/l)
2-Hexanone (UG/l)
Tetrachloroethene (UG/l)
1,1,2,2-Tetrachloroethane (UG/l)
Toluene (Ue/l)
Chlorobenzene (UG/l)
Ethylbenlene (\JG/l)
Styrene (UG/l)
Xylenes (total) (UG/l)
Note: (I) Results are reported with qualifiers (lllboratory QUDlifler/Oata Validation Quulltter) to the right of the vulue.
. '.
,. .-
UK -GWHU060- DAD 11/0Z/90
-------..--............--..--..-..
4.
JI
z.
JI
-------
PRIVATE WELLS
..
"-
-------
, "
I; !:
ANALYTICAL DA'A REPOR'
Voodstock landfill Rl/fS
Voodstock, II IInol s
. Hatrlx: PV Type: Mil
Generated by: CAU
Date Issued: 10-HAY-91
Parameter UK.PWOI-OI 07/24/90 VK-PV02-01 07/24/90 VK-PVQ3-01 07/24/90 UK-PV04-01 07/24/90 UK-PU04-91 07/24/90
-.--....--.------------------- ......--...------------- -.----.-.......-.--...-. ------------------------ ---.-.----.--.----.----. ------...----------.----
Aluninllll (UG/l) 50. UI 50. UI 52. K/ 51. K/ 50. U/
Antimony (UG/l) 5. U/ 5. UI 5. U/ 5. U/ 5. U/
Arsenic (UG/l) 2.3 KI 2. us/ 2. UI 2.6 KI 2. UI
Bar hili (UG/l) 63. K/ 10. U/ 98. K/ 134. K/ 137. K/
Beryl I lun (UG/l) 5. UI 5. UI 5. U/ 5. U/ 5. UI
Cad1llun (UG/l) 0.2 UI 0.2 UI 0.2 UI 0.2 U/ 0.2 U/
Calclun (UG/l) 124000. I 1300. KI 82400. I 109000. I 109000. I
Chromlun, total (UG/l) 0.96 IC/U 0.52 K/U 0.53 K/U 0.38 K/U 0.44 K/U
Cobal t (UG/l) 10. UI 10. UI 10. U/ 10. U/ 10. U/
Copper (UG/l) 10. U/ 10. U/ 10. U/ 10. U/ 10. UI
Iron (UG/U 2430. 1 107. 1 996. I 2500. / 2680. /
lead (UG/l) 3. U/ 3. UI 3. U/ 3. U/ 3. U/
Hagneslun (UG/l) 68400. I 1000. U/ 37200. / 60000. / 61200. I
Hangenese (UG/l) 119. 1 10. UI 57. I 34. I 32. /
Mercury (UG/l) 0.2 UI 0.2 U/ 0.21 1 0.2 U/ 0.2 UI
Nickel WG/l) 20. U/ 20. UI 20. U/ 20. u/ 20. u/
Potasslun (UG/l) 1670. ICN/J 530. KN/J 1190. IeN/J 1110. KN/J 1020. IeN/J
Selenlun (UG/L) 2. u/ 2. UI 2. USI 2. U/ 2. U/
Sit ver (UG/L) 0.5 US/UJ 0.5 US/UJ 0.5 US/UJ 0.5 US/UJ 0.5 US/UJ
Sodlun (UG/l) 15200. 1 306000. 1 34000. I 9500. / 9100. /
Thatllun (UG/l) 3. U/ 3. USI 3. U/ 3. u/ 3. IeS/
Vanadlun (UG/l) 50. U/ 50. UI 50. U/ 50. U/ 50. UI
Zinc (UG/l) 284. 1 50. 1 23. I 132. I 133. /
Cyanide (UG/l) 10. U/ 10. UI 10. UI 10. U/ '0. U/
Note: (1) Results are reported with qualifiers (laboratory Qualifier/Data Validation Qualifier) to the right of the vulue.
-------
Hatrlx: PU
Type: HTl
P8rameter
..-...-.------------------------
UK-PUFBOI-01 01/24/90
... -- -... ---.""''''. -...- --.... ----
Alunlnun (UG/L)
Ant hnony (UG/L)
Arsenic (UG/L)
B8r1un (UG/l)
Beryfllun (UG/U
Cadniun (UG/L>
Calclun CUG/L)
Chromlun, total
C0b81 t (UIi/L)
Copper (UG/L)
'ron (UG/L)
le8d (UG/L)
M8gneslun (UG/L)
H8ng8nese (UG/L)
Hercury (UG/l)
Nldel (UG/l)
Pot8sslun (UG/L)
Seleniun (UG/L)
Sit ver (UG/L)
Sodh.. (UG/L)
Th8111un CUG/U
V8nadlun (UG/l)
Zinc (UG/l)
Cyanide (UG/L)
50.
5.
2.
10.
5.
0.2
1000.
0.51
10.
10.
20.
3.
1000.
10.
0.2
20.
100.
2.
0.5
1000.
3.
50.
10.
10.
(UG/L)
UI
U/
U/
UI
UI
UI
U/
K/U
U/
U/
U/
U/
U/
U/
U/
U/
UN/UJ
U/
U/UJ
U/
U/
U/
U/
U/
ANALYTICAL DATA REPORT
Uoodstock Landfill RI/FS
UOodstock, illinois
2
Note: (1) Resut ts are nported wi th qual if lers (l.nborotory Quat If ler/D8t8 Valldot Ion QUIlt I tier> to the right of the vatue.
, '.
1'(":
-------
SEDIMENT
:.-.
-------
ANALYTICAL OATA REPORT
Uoodstock landfill Rl/fS
lIoodstock, Illinois
Hatrix: PII Type: vac
Generated by: CAU
Date Issued: 10-HAY-91
Peremeter ur-P\IOI-01 07/24/90 UK'PII02-01 07/24/90 UK-PIIO]-OI 07/24/90 \IK.PII04.01 07/24/90 ur-PU04-91 07/24/90
----...... --..-.. --....... ----.... --........... ....-----..-------------.. --------..--........---..-........- ........---------------. .--------..-------------- --------------..-..----....
Chloromethane (IIG/l) 2. UI 2. U/ 2. III 2. III 2. UI
Bromomethsne (UG/l) 2. III 2. UI 2. UI 2. UI 2. ul
Vinyl chloride (IIG/l) 2. III 2. UI 2. UI 2. UI 2. III
Chloroethane (IIG/l) 2. UI 2. UI 2. . UI 2. III 2. III
Hethylene chloride (UG/l) 6. /U 1. IU 1. IU 1. IU 1. UI
Acetone (UG/l) 5. UI 5. II/ 5. ul 5. UI 5. UI
Carbon disulfide (UG/l) ]. III ]. UI 3. UI 3. UI 3. UI
1,l-Olchloroethene (UG/l) 2. UI 2. UI 2. III 2. UI 2. UI
1,l'Olchloroethane (UG/l) 2. UI 2. II/ 2. III 2. UI 2. UI
1,2'0lchloroethene (total) (UG/l) 2. UI 2. III 2. UI 2. UI 2. UI
Chloroform (UG/l) 2. UI 2. UI 2. UI 2. UI 2. UI
1,2-OI~hloroethane (IIG/l) 2. UI 2. III 2. UI 2. III 2. UI
2-Butanone (UG/l) 5. U/R 5. U/R 5. UI 5. U/R 5. U/R
I,I,I-Trlchloroethane (UG/L) 2. III 2. UI 2. UI 2. UI 2. UI
Carbon tetra~hlorlde (UG/l) 2. UI 2. UI 2. UI 2. UI 2. UI
Vinyl acetate (UG/l) 5. U/ 5. U/ 5. UI 5. UI 5. UI
Bromodlchloromethane (UG/l) 2. U/ 2- UI 2. UI 2. UI 2. UI
1,2'OI~hloropropane (UG/L) 2. UI 2. U/ 2. UI 2. UI 2. UI
cls-I,J'OI~hloropropene (UG/L) 2. UI 2. U/ 2. UI 2. UI 2. UI
Trlchloroethene (UG/l) 2. UI 2. U/ 2. III 2. III 2. UI
Olbromo~hloromethane (UG/l) 2. III 2. U/ 2. III 2. UI 2. III
1,I,2-Trl~hloroethane (UG/l) 2. UI 2. II/ 2. III 2. UI 2. UI
Henrene (UG/l) 2. UI 2. III 2. UI 2. III 2. UI
trans-I,3-DI~hloropropene (UG/l) 1. UI 1. III 1. III 1. UI 1. U/
Bromoform (IIG/l) 2. U/ 2. U/ 2. III 2. UI 2. UI
4-Hethyl-2-pentanone (IIG/l) 2. UI 2. UI 2. III 2:. UI 2. UI
2-Hexenone (UG/l) 5. UI 5. U/ 5. III 5. UI 5. UI
Tetrachloroethene (UG/l) 2. UI 2. U/ 2- UI 2. UI 2. U/
1,I,2,2-Tetrachloroethane WG/l) 2. UI 2. U/ 2. UI 2. UI 2. II/
Toluene (UG/L> 2. U/ 2. U/ 2. UI 2. UI 2. UI
Chlorobenrene (UG/l) 2. II/ 2. U/ 2. UI 2. UI 2. U/
Ethylbenzene (UG/l) 2. UI 2. U/ 2. UI 2. III 2. III
Styrene (UG/l) 1. UI 1. U/ 1. U/ 1. U/ 1. U/
Xylenes (total) (UG/l) 2. U/ 2. U/ 2. UI 2. UI 2. lI/
A~roleln (UGIt) 25. U/R 25. U/R 25. UI 25. lI/R 25. lI/R
A~rylonttrile (lIC/l) 25. U/ 25. III 25. UI 25. UI 25. UI
Hote: (I) Results ore reported with qualifiers (lohorotory Qualifier/Data Val idatlon Qualifier) to the right 0.' the vallie.
-------
ANALYTICAL nATA REPORT 2
Uoodstock lnndfill RI/FS
Uoodstock, IllInois
Murlll: PU Type: vac
Parllll1eter UK-PUFB01-01 07/24/90 UK-PUrB01-01 07/24/90
--.-.....---..............-... -......----.-..-.---...- .-----...---------------
Chloromethane (UG/l) 2. U/ 2. U/
Bromomethane (UG/l) 2. U/ 2. U/
Vinyl chloride (UG/l) 2. U/ 2. U/
Chloroethane (UG/l) 2. U/ 2. U/
Methylene chloride (UG/l) 0.5 J/ ,. U/
Acetone (UG/l) 6. B/U 5. U/
Carbon disulfide (UG/l) 3. u/.. 3. U/
1,'-Dlchloroethene (UG/l) 2. U/ 2. U/
','-Olchloroethane (UG/l) 2. U/ 2. U/
1,2-Dlchloroethene (total) (UG/I) 2. U/ 2. U/
Chloroform (UG/l) 4. / 4. /
1,2-0lchloroethane (UG/l) 2. U/ 2. U/
2-Butanone (UG/l) 5. U/R 5. U/R
',I,1-Trlchloroethane (UG/l) 2. U/ . 2. U/
Carbon. tetrachloride (UG/l) 2. U/ 2. U/
Vinyl acetate (UG/l) 5. U/ 5. U/
Bromodlchloromethane (UG/l) 2. U/ 0.5 J/
',2'Dlchloropropane (UG/l) 2. U/ 2. U/
cls",3'Dlchloropropene (UG/l) 2. U/ 2. U/
Trlchloroethene (UG/l) 2. U/ 2. U/
Dlbromochloromethane (UG/l) 2. U/ 2. U/
',1,2'Trlchloroethane (UG/l) 2. U/ 2. U/
Benzene (UG/l) 2. U/ 2. U/
trans",3-Dlchloropropene (UG/l) 1. U/ 1. U/
Bromoform (UG/l) 2. U/ 2. U/
4-Methyl'2'pentanone (UG/l) 2. U/ 2. U/
2-Hex8none (UG/l) 5. U/ 5. U/
Tetr8chloroethene (UG/l) 2. U/ 2. U/
1,',2,2-Tetrachloroethane (UG/l) 2. u/ 2. U/
Toluene (UG/I) 2. U/ 2. U/
Chlorobenzene (UG/l) 2- U/ 2. U/
Ethylbenzene (UG/l) 2. U/ 2. U/
Styrene (UG/l) 1. II/ 1. U/
Kylenes (total) (UG/l) 2. U/ 2. U/
Acrolein (UG/l) 25. U/R 25. U/R
Acrvlonltrlle (UG/l) 25. u/ 25. U/
Note: (1) Results are reported \lith qualifiers (l.aborRtory Qualifier/Date Validation Qualifier) to the right 01 the value.
, '"
-------
SEDIMENT
.',
..
".
-------
, 0'
I ~ t1
ANALYTICAL DATA REPORT
Uoodstock landfill RI/FS
Uoodstock, illinois
Hatrl x: 50 Type: SliNO HTl
Generated by: CAU
08te Issued: 10-HAY-91
Parameter UK.S001-01 09/06/90 UK-S001-91 09/06/90 UK-S002-01 09/06/90 UK-S003-01 09/06/90 WK'SD04'01 09/06/90
..__e_.--.......-...."....""-- ...-------.-.-.-........- -----.-..-.---.-.-.----- -.- .......-..- .........-......- -.-......-......----.....-.. ......---...--........ w_-........
Alunlnun (HG/ICG) 8870. / 7470. / 9630. / 15600. / 13800. /
Antimony (HG/ICG) ]].7 UN/UJ ]4. UN/UJ ]3.3 UN/UJ 49. UN/UJ 21.4 UN/UJ
Arsenic (HG/ICG) 6.3 K/ 7.5 / 12.7 / 24. S/ 9.7 /
Barlun (HG/KG) 209. / 223. / 243. / 316. / 238. /
Beryllium (HG/KG) 3.4 U/ ].4 U/ ].] U/ 1,.9 U/ 2.1 U/
Cadnlum (HG/ICG) ].1, U/ ].4 U/ ].] U/ 1,.9 U/ 2.1 U/
Calcium (HG/KG) ]3200. / ]6500. / 43300. / 112000. / 66800. /
Chromlun, total (HG/KG) 15.5 / 14.3 / 28. / 30.1, / 1,1.4 /
Cobalt (HG/ICG) 6.7 U/ 6.8 U/ 7.3 ICIU 10.8 K/U 9.4 IC/U
Copper (MG/ICG) 28.] / 29.] / 99.3 / 28.1, / 141,. /
Iron (HG/ICG) 20800. / 21300. / 28000. / 61000. / 56300. /
Lead (HG/ICG) 44.9 / 50.2 / 109. / 43.1 5/ ]0.5 5/
Hagneslum (HG/KG) 4310. / 1,310. / 6500. / 14100. / 13800. /
Hang.nese (HG/KG) 357. / 1,45. / 531. / 616. / 747. /
Mercury (MG/KG) 0.15 / 0.14 lI/ 0.15 / 0.2 u/ 0.] /
Nickel (MG/KG) ]1.6 / 17.7 K/ 107. / 24.5 K/ 274. /
Potassium (HG/KG) 821. K/ 694. K/ 1110. K/ 1,210. K/ 1600. K/
Selenium (HG/KG) 2.4 K/ 1.6 KS/ 1.9 K/ 2.9 1(/ 1.7 K/
Sliver (HG/KG) 6.7 U/ 6.8 U/ 6.7 U/ 1,9. U/ 4.] U/
SodlUli (HG/KG) 1350. U/ 1360. U/ 1]30. U/ 1960. U/ 855. U/
Ihailium (HG/KG) 2.5 K/ 2. U/ 2. U/ ].7 KS/ 2.1 K/
Vanadium (HG/KG) ]4.] / ]4. U/ ]3.3 U/ 1,9. U/ 31.6 /
Zinc (MG/KG) 196. / 212. / 806. / 175. / 715. /
Cyanide (HG/KG) 8.4 U/ . 8.5 U/ 8.] U/ 12.2 U/ 5.] U/
10tal Organic Carbon (HG/KG) 16000. >/ 16000. >/ 16000. >/ 16000. >/ 16000. >/
Cation Exchange Capacity (HEQ/L) 16.1 / 16.] / 19.1, / '7.86 / 5.1, /
Totel Sol Ids (X) 29.7 / 29.4 / ]0. / .20.4 / 1,6.8 /
Note; (1) Results are reported with qUAlifiers (laboratory Qualifier/Date Validation Qualifier) to the right 0' the value-
-------
ANALYTICAL DATA REPORT 2
Uoodstock Landfill RI/fS
Uoodstock, It tlnols
Hatrlx: SD Type: SlINO HIL
Parameter UK'S005-01 09/06/90 UK'S006-01 09/06/90 UK-S007-01 09/06/90 UK-S008-01 09/06/90 UK-SOIO-OI 0~/02/91
-------..------..--------------- .-......-.......... ....---....-....-- --.......- -...... .....----- ....----- --....-.... --.. -- -.. --.. ....-........ ---- -..--.. --.. ---...... --.... -.. .. .. ................ . .... .. .... .... ............
Aluminum (HG/KG) 6270. I 8850. / 6210. I 12500. / 5560. /
Antimony (HG/KG) 25.4 UN/UJ 24.4 UN/UJ 15.8 UN/UJ 56.5 UN/UJ 49.6 U/
Arsenic (HG/KG) 18. I / 7. / 2.3 K/ 5.3 K/ 11. 1 K/
8Brlum (HG/KG) 203, / 146. / 46.8 K/ 100. K/ 112. K/
Beryllium (HG/KG) 2.5 U/ 2.4 U/ 1.6 U/ 5.6 U/ 5. U/
Cadnlum (HG/KG) 2.5 U/ 2.4 U/ 1.6 U/ 5.6 U/ 5. U/
Calcium (HG/KG) 136000. / 99800. / 61400. / 18500. / 35100. N/J
Chromhn, tote I (HG/KG) 11.7 / 13.2 / 8.9 / 18.1 / 9.9 U/
Cabal t (KG/KG) 6.6 K/U 5.8 K/U 5.1 K/U 11.3 U/ 9.9 U/
Copp!r (KG/KG) 61. / 26.8 / 10.7 / 29.4 / 12.9 K/
Iron (HG/KG) 46300. / 16700. I 10600. / 14600. / 18200. I
Lead (KG/KG) 46.8 5/ 22.7 51 11.3 5/ 44.9 S/ 12.6 5./
Hagneslum (HG/KG) 16100. / 4270. / 29000. / 6570. / 6880. /
Hanganese (HG/KG) 605. / 558. I 208. / 11.7. I 148. /
Hercury (KG/KG) 0.1 U/ O. I U/ 0.06 U/ 0.23 U/ 0.28 U/
Nickel (KG/KG) 42.2 / 9.7 U/ 6.3 U/ 45.2 KI 19.8 U/
Potassium (HG/KG) 1380. IC/ 1250. K/ 692. K/ 1610. K/ 7M. K/
Selenium (HG/KG) 1. U/ 0.98 US/ 0.63 U/ 2.3 UI 2.3 US/
5 It ver (KG/KG) 5.1 U/ 4.9 UI 3.2 U/ 11.3 U/ 9.9 U/
SodlUil (HG/KG) 1020. U/ 975. U/ 939. KI 5490. K/ 2040. K/
Thallium (HG/KG) 1.6 K/ 1.5 U/ 0.95 U/ 3.4 U/ 3.4 U/
Vanadlu. ("G/KG) 25.4 U/ 26.8 ' 1 23.4 I 56.5 U/ 49.6 U/
Zinc ("G/KG) 432. / 168. / 42.7 / 150. / 108. /
CyanIde ("G/KG) 6.4 U/ 6.1 U/ 3.9 U/ 14.1 U/
Total Organic Carbon (KG/KG) 16000. >/ 16000. >1 16000. >/ 16000. >/
Cltlon Exchlnge Clpaclty (KEO/L) 5.08 / 11.5 / 5.11 I 12.7 /
Total Sol Ids (X) 39.3 / 41. / 63.3 / 17.7 / 14.3 /
Note: (1) Results are reported with qllnlifiers (taboratory Qualifier/Data Volldntion Qualifier) to the right of the volue-
, "
II (I
-------
, .'
, .
ANALYTICAL DATA REPORT 1
Uoodstock Landfill RI/FS
Uoodstock. Illinois
Hatrlx: SO Type: SUNO HTl
Parameter ~-SOI0-91 04/02/91 UK-soI1.01 04/03191 WK.S012.01 04/03191 ~-So13-01 04/03/91 UK'S014.01 04/01/91
__..e_____-.----------.-"'---"'- -.------------------.--- ---------------.-------- ---------------------... ------.......-------.----.-- ......... ............ ... ... ... ... ... ... ... ...... ... ...... "''''''' - ...
Alunlnun (HG/KG) 8390. / 8850. I 12300. I 8400. I 11600. I
Antimony (HG/KG) 41. U/ 57. UI 22.9 UI 50.7 U/ 19.5 U/
Arsenl c (HG/KG) 12.9 / 12.8 I 7.1 I 6.9 K/ 5.5 /
Baritm (HG/KG) 152. K/ 165. K/ 172. / 97.3 KI 161. /
8erylliun (MG/KG) 4.1 U/ 5.7 U/ 2.1 UI 5.1 U/ 1.9 U/
Cadniun (MG/KG) 4.1 U/ 5.7 U/ 2.3 U/ 5.1 UI 1.9 U/
Calclun (HG/KG) 38400. N/J 54400. N/J 29300. N/J 22000. N/J 11000. N/J
Chromlun. total (HG/KG) 8.6 I 13.2 I 18.2 / 10.1 U/ 15.6 I
Cobatt (HG/KG) 8.2 U/ 11.4 U/ 6.9 KI 10.1 UI 7. KI
Copper (HG/KG) 14.8 KI 31.9 I 17.8 I 12.2 KI 17.5 I
Iron (HG/KG) 25000. / 34500. I 29900. / 16100. / 15400. /
Lead (HG/KG) 73. *1 58.3 .' 18.7 *1 450. *1 42.1 S*/
Hagneslun (MG/KG) 8950. I 10600. I 6810. I 3270. KI 3610. /
Manganese (MG/KG) 152. I 270. I 293. I 218. I 1260. I
Mercury (MG/KG) 0.19 UI 0.29 U/ 0.11 UI 0.27 U/ 0.11 U/
Nickel (HG/KG) 16.4 UI 28.5 KI 16.9 KI 20.3 UI 16.8 I
Potasslun (MG/KG) 1020. KI 1630. KI 1460. KI 1050. K/ 1590. KI
Selenlun (HG/ICG) 1.4 ICI 2.3 KSI 1.6 ICI 2.4 USI 0.96 KI
Sliver (HG/KG) 8.2 UI 11.4 UI 4.6 U/ 10.1 UI 3.9 U/
Sodlun (HG/ICG) 2000. KI 2300. KI 914. UI 2030. UI 779. UI
Thalt lun (HG/KG) 2.1 U/ 3.1, UI 1.2 USI 3.6 U/ 1.1 UI
Vanadlun (HG/KG) 41. U/ 57. U/ 22.9 UI 50.7 UI 26.1 /
Zinc (MG/KG) 140. I 513. I 87.8 I 51.7 / 93.9 /
Cyanide (MG/KG)
Total Organic Carbon (HG/KG)
Cation Exchange Capacity (HEO/L)
Total Solids 00 21.4 I 13.9 / 34.9 / 14.6 I 35.4 I
Note: (I) Results are reported \lith qllalifier~ °(lnhoratory Qualifier/Datil Validation Qualifier) to the right 0' the value.
-------
ANALYTICAL DATA REPORT 4
Uoodstock Landfill RllfS
UOodstock, Illinois
Hatrlx: SO Type: SlINO Hfl
Parameter \11(-5015'01 04/0]/91 \11(-5016-01 04/0]/91
....-----.......--......-.-.-. ---...---------.-------- ------------------------
Aluminum (HG/KG) 12800. / ]4]0. /
Antimony (HG/KG) 42. U/ 41.7 UI
Arsenic (HG/KG) 9.3 I 12.5 I
Barium (KG/KG) '29. KI 79.2 kl
Beryllium (KG/KG) 4.2 U/ 4.2 UI
Cachlum (HG/KG) 4.2 UI 4.2 U/
Calcium (HG/KG) 65000. N/J 2]600. N/J
Chromium, total (HG/KG) 17.6 I 8.] UI
Cobsl t (HG/KG) 11.7 K/ 8.] UI
Copper (HG/I(G) 26.9 I 15. KI
Iron (HG/KG) 22700. I 16500. I
Lead (HG/KG) 56.6 ./ 73. .,
Hagneslum (HG/KG) 18500. / ]160. K/
Hanganese (HG/KG) 571. I 1111. I
Mercurv (HG/KG) 0.2 UI 0.2] UI
Nickel (HG/KG) 16.8 KI 16.7 UI
Potassium (HG/KG) 2020. KI 1510. KI
Selenium (HG/KG) 1.7 USI 1.8 USI
5 II ver (HG/I(G) 8.4 UI 8.] UI
Sodium (HG/KG) "40. I 1670. UI
Thallium (HG/KG) 2.6 UI 2.7 UI
Vanadium (HG/KG) 42. UI 41.7 UI
Zinc (HG/KG) 15]. I 131. I
Cyanide (HG/KG)
Total Orgenlc Carbon (HG/KG)
Cation Exchange Capacltv (HEO/L)
Totel Solids (X) 19.7 I 17.] I
Note: (1) Re~ults B'-e reported with qualifiers CtoborDtory oUDllfler/ODtB VDlldDtion OUDlifler) to the right of the value.
It!,
-------
, "
t: I
ANALYTICAL DATA REPORT
Uoodstock Landfill R IIFS
uoods t od, illinois
HUrlll: SO Type: VOC
Generated by: CAU
Date Issued: 10-HAY-91
Parameter wr'SOOI-01 09/06/90 UK'SDOI-91 09/06/90 UK-SD02'01 09/06/90 UK-SD03-01 09/06/90 UK-SDO'-OI 09/06/90
._...._e_----"-.--------------- .....--.. ---.-.... --_............- ...-- ------.. -_......- -..-----.... ......--.----------------..- ...... -.................. ........ .. .. .. ......... ------....--------..---....
Chloromethane (UG/KG) 33. U/ 30. U/ 32. U/ 37. U/ 20. U/
Bromomethane (UG/KG) 33. U/ 30. U/ 32. U/ 37. U/ 20. U/
Vinyl chloride (UG/KG) 33. U/ 30. U/ 32. U/ 37. U/ 20. U/
Chloroethane (UG/KG) 33. U/ 30. U/ 32. U/ 37. U/ 20. U/
Hethylene chloride (UG/KG) '7. B/U 51. 8/U 64. B/II '3. B/U 57. 8/U
Acetone (UG/KG) 33. U/ 74. B/U 140. B/U 130. B/U 87. 8/U
Carbon disulfide (UG/KG) 16.5 U/ 15. U/ 16. U/ 18.5 U/ 10. U/
1,l-Dlchloroethene (UG/KG) 16.5 u/ 15. u/ 16- u/ 1B.5 U/ 10. UI
1,I-Dlchloroethane (UG/KG) 16.5 U/ 15. U/ 16. U/ 16.5 U/ 10. U/
1,2-0Ichloroethene (total) (UG/KG) 16.5 U/ 15. U/ 16. U/ 18.5 U/ 10. u/
Chloroform (UG/KG) 16.5 U/ 15. U/ 16. U/ 18.5 U/ 10. u/
1,2'0ichloroethane (UG/KG) 16.5 u/ 15. u/ 16. u/ 18.5 U/ 10. u/
2-8utanone (UG/KG) 33. u/ 30. U/ 32. U/ 15. J/ 20. U/
1,1,1-Trlchloroethane (UG/KG) 16.5 u/ 15. U/ 16. U/ 16.5 U/ 10. U/
Carbon tetrachloride (UG/KG) 16.5 U/ 15- U/ 16. U/ 18.5 U/ 10. U/
Vinyl acetate (UG/KG) 33. U/ 30. U/ 32. , U/ 37. U/ 20. U/
Bromodlchloromethane (UG/KG) 16.5 U/ 15. U/ 16. U/ 16.5 U/ 10. U/
1,2'Dlchloropropane (UG/KG) 16.5 U/ 15. U/ 16. U/ 18.5 U/ 10. U/
cla-I,3-0Ichloropropene (UG/KG) 16.5 U/ 15. U/ 16. U/ 18.5 U/ 10. U/
Trlchloroethene (UG/KG) 16.5 U/ 15. U/ 16. U/ 18.5 U/ 10. U/
Dlbromochloromethane (UG/KG) 16.5 U/ 15. U/ 16. U/ 16.5 U/ 10. U/
1,1,2'Trlchloroethane (UG/KG) 16.5 U/ 15. U/ 16. U/ 18.5 U/ 10. U/
Benzene (UG/KG) 16.5 U/ 15. U/ 16. U/ 18.5 U/ 10. U/
trans.1,3'0Ichloropropene (UG/KG) 16.5 U/ 15. U/ 16. U/ 18.5 U/ 10. u/
Bromoform (UG/KG) 16.5 U/ 15. U/ 16. U/ 16.5 U/ 10. U/
4-Hethyl-2-pentanone (UG/KG) ]]. U/ ]0. U/ 32. U/ 37. U/ 20. U/
2-Hellanone (UG/KG) ]]. U/ 30. U/ 32. U/ 37. U/ 20. U/
Tetrachloroethene (UG/KG) 16.5 U/ 15. U/ 16. U/ 16.5 U/ 10. U/
1,I,2,Z-Tetrachloroethane (UG/KG) 16.5 U/ 15. U/ 16. U/ 16.5 U/ 10. u/
Toluene (UG/KG) 16.5 U/ 15. U/ 12. J/ 17. J/ 14. /
Chlorobenzene (UG/KG) 16.5 U/ 15. U/ 16. U/ 16.5 U/ 10. U/
Ethylbenzene (UG/KG) 16.5 U/ 15. U/ 16. U/ 18.5 U/ 10. U/
Styrene (UG/KG) 16.5 U/ 15. U/ 16. U/ 18.5 U/ 10. U/
Xylenes (total) (UG/KG) 16.5 U/ 15. U/ 16. U/ 18.5 U/ 10. II/
NOle: (1) Results ore ff'ported wllh quolifiers (loborolory Quollfler/Deto Validation Qualifier) to the right of the value.
-------
ANALYTICAL OATA REPORT 2
UOodstock lendflll Rl/fS
Uoodstock, Illinois
Hetrlll: SO TVpe: VOC
Peremeter UK-SD05-01 09/06/90 UK-S006-01 09/06/90 UK-S007-01 09/06/90 UK-S008-01 09/06/90
----.-.............- -...................... .....- .4__._.._----..----------- ------....----.-----.---- ---------..----...----....... -..- -....-... -. -.................. -....-
Chloromethane (UG/KG) 28. UI 23. U/ 13. U/ 77. UI
Bromomethene (UG/KG) 28. UI 23. U/ 13. U/ 77. U/
VInyl chloride (UG/KG) 28. U/ 23. U/ 13. UI 77. UI
Chloroethene (UG/KG) 28. UI 23. UI 13. UI 77. UI
Hethylene chloride IUG/KG) 28. B/U 21. B/U 17. B/U 220. B/U
Acetone (UG/KG) 62. B/U 55. B/U 32. B/U 280. B/U
C8rbon dIsulfide (UG/KG) ". UI 11.5 UI 6.5 UI ]8.5 U/
1,1-0Ichloroethene IUG/KG) ". UI 11.5 UI 6.5 U/ 38.5 U/
1,1'Olchloroeth8ne (UG/KG) Ii,. UI 11.5 U/ 6.5 U/ 38.5 UI
1,2-0Ichloroethene (tot81) WG/KG) 14. UI 11.5 UI 6.5 UI 38.5 UI
Chloroform (UG/KG) 14. UI 11.5 UI 6.5 u/ ]8.5 U/
1,2-0lchloroethene (UG/KG) 14. U/ 11.5 U/ 6.5 U/ 38.5 U/
2-Rutenone lUG/KG) 28. U/ 23. UI 13. U/ 39. BJ/U
1,1,1-Trlchloroeth8ne (UG/KG) 14. U/ 11.5 U/ 6.5 U/ 38.5 U/
C8rbon tetr8chlorlde (UG/KG) 14. U/ 11.5 U/ 6.5 U/ 38.5 U/
VInyl 8cet8te (UG/KG) 28. UI 23. U/ 13. U/ 77. UI
8romodlchloromethene (UG/KG) 14. U/ 11.5 UI 6.5 UI 38.5 UI
1,Z-Dlchloropropene (UG/KG) 14. U/ 11.5 U/ 6.5 U/ 38.5 UI
cll'1,3'Dlchloropropene (UG/KG) 14. U/ 11.5 U/ 6.5 U/ 38.5 U/
Trlchloroethene (UG/KG) 14. U/ 11.5 U/ 6.5 U/ 38.5 U/
Dlbromochlorometh8ne (UG/KG) 14. U/ 11.5 U/ 6.5 UI 38.5 U/
1,1,Z-Trlchloroeth8ne (UG/kG) 14. U/ 11.5 UI 6.5 U/ 38.5 U/
Benzene (UG/kG) 14. UI 11.5 U/ 6.5 UI 38.5 UI
trlnl'1,3-Dlchloropropene (UG/KG) 14. U/ 11.5 U/ 6.5 U/ 38.5 U/
8romofor~ (UG/KG) ". U/ 11.5 U/ 6.5 UI 38.5 U/
4-Hethyl-Z-pent8none (UG/KG) 28. U/ 23. U/ 13. U/ 77. U/
2-Hexenone (UG/KG) 28. U/ 23. U/ 13. U/ 77. U/
Tetr8chloroethene (UG/KG) 14. U/ 11.5 U/ 6.5 UI 38.5 U/
1,1,2,2-Tetr8chloroeth8ne (UG/kG) 14. UI 11.5 U/ 6.5 U/ 38.5 U/
Toluene (UG/KG) 3. J/ 3. J/ 7. / 92. /
Chlorobenzene (UG/KG) 14. tI/ 11.5 U/ 6.5 U/ 38".5 U/
Ethylbenzene (UG/KG) 14. tI/ 11.5 UI 6.5 u/ 38.5 U/
Styrene (UG/KG) 14. U/ 11.5 UI 6.5 tII 38.5 U/
Xylenes (tot81) (UG/KG) 14. tll 11.5 UI 6.5 U/ 38.5 U/
.
Note: (I) Results lire reported with qualifiers Ilaboratory Qualifier/Oete ValidAtion Qualifier) to the right of the value.
, '.
,. .
-------
, 0'
t: I
Matrix: 50 Type: 5VOC
Generated by: CAU
Date Issued: 10-HAY-91
ANALYTICAL DATA REPORT
Uoodstock lendflll RI/fS
Uoodstock, Illinois
.......--.....--.......-..----------
UK-SOOI.01 09/06/90
..........--..-.. ..-..--.... -- .........
Parameter
UK-soOI-91 09/06/90
-....-..--- --- -- -------..-....
Phenol (UG/KG) 1089.
bls(2-Chloroethyl) ether (UG/KG) 1089.
2-Chlorophenol (UG/KG) 1089.
1,3-0ichlorobenzene (UG/KG) 1089.
1,4.olchlorobenzene (UG/KG) 1089.
Benzyl Alcohol (Ue/KG) 1089.
1,2'Olchlorobenzene (UG/KG) 1089.
2'Hethylphenol (UG/KG) 1089.
bls(2'Chtorolsopropyl)ether (UG/KG) 1089.
4-Hethytphenot (UG/KG) 1089.
N'Nltroso'dl'n'dlpropylamine (UG/KG) 1089.
Hexachloroethane (UG/KG) 1089.
Nitrobenzene (UG/KG) 1089.
Isophorone (UG/KG) 1089.
2-Nltrophenol (UG/KG) 1089.
2,4-0lmethylphenol (UG/KG) 1089.
Benrolc Acid (UG/KG) 5280.
bls(2'Chtoroethoxy)methane (UG/KG) 1089.
2,4-0lchtorophenol (UG/KG) 1089.
1,2,4-Trlchlorobenzene (UG/KG) 1089.
Naphthatene (UG/KG) 1089.
4'Chloroanltlne (UG/KG) 1089.
Hexachlorobutadlene (UG/KG) 1089.
4-Chtoro-3-methytphenot (UG/KG) 1089.
2'Hethylnaphthatene (UG/KG) 1089.
Hex8chtorocyclopentadlene (UG/KG) 1089.
2,4,6'Trlchlorophenot (UG/KG) 1089.
2,4,5'Trlchtorophenol (UG/KG) 5280.
2'Chtoronaphthatene (UG/KG) 1089.
2'Nltroanltlne (UG/KG) 5280.
Olmethylphthalate (UG/KG) 1089.
Acenaphthylene (UG/KG) 1089.
2,6'Oinltrotoluene (UG/KG) 1089.
3-Nitroaniline (UG/KG) 5280.
Acenaphthene (UG/KG) 1089.
2.4'Oinitrophenol (UG/KG) 5280.
4-Nitrophenol (IIG/KG) 5280.
Note: (I) Results ere reported with qual ifiers
UI 1188. UI 1100.
UI 1188. U/ 1098.9
U/ 1188. UI 1098.9
U/ 1188. U/ 1098.9
UI 1188. U/ 1098.9
U/ 1188. U/ 1098.9
U/ 1188. U/ 1098.9
U/ 1188. U/ 1098.9
UI 1188. U/ 1098.9
U/ 1188. U/ 180.
U/ 1188. U/ 1098.9
U/ 1188. U/ 1098.9
U/ 1188. U/ 1098.9
U/ 1188. U/ 1098.9
U/ 1188. U/ 1098.9
UI 1188. U/ 1098.9
U/ 5760- UI 190.
U/ 1188. U/ 1098.9
UI 1188. U/ 1098.9
U/ 1188. U/ 1098.9
U/ 1188. U/ 1098.9
UI 1188. U/ 1098.9
UI 1188. U/ 1098.9
U/ 1188. U/ 1098.9
U/ 1188. U/ 1098.9
U/ 1188. U/ 1098.9
UI 1188. U/ 1098.9
UI 5760. U/ 5328.
U/ 1188. U/ 1098.9
U/ 5760. U/ 5]28.
UI 1188. U/ 1098.9
UI 1188. U/ 1098.9
II/ 1188. U/ 1098.9
II/ 5760. UI 5]28.
U/ 1188. U/ 1098.9
III 5760. U/ 5328.
III 5760. U/ 5328.
(laboratory Qualifier/Date Validation Quatlfler)
UK-SOOl-OI 09/06190
-..----------------------
J/
II/
U/
U/
U/
U/
U/
U/
U/
J/
U/
U/
U/
U/
U/
U/
J/
U/
U/
U/
U/
U/
U/
U/
U/
U/
U/
II/
U/
U/
UI
U/
U/
U/
U/
III
II/
to the right of
UK-S003.01 09/06/90
.......--------..--.... ---- ----
UK-S004-0t 09/06/90
1485.
1485.
1485.
1485.
1485.
1485.
1485.
1485.
1485.
1485.
1485.
14115.
1485.
14115.
1485.
1485.
7200.
1485.
14115.
1485.
1485.
1485.
1485.
1485.
1485.
14115.
01485.
7200.
1485.
7200.
1485.
1485.
1485.
7200.
1485.
7200.
7200.
the value.
U/
II/
U/
U/
U/
U/
UI
U/
II/
II/
II/
U/
II/
UI
U/
II/
II/
II/
U/
U/
II/
II/
U/
U/
II/
U/
II/
U/
U/
II/
III
U/
III
II/
UI
III
UI
-..--....-.. ----.............. _..-....
627.
627.
627.
627.
627.
627.
100.
627.
627.
627.
627.
627.
627.
627.
627.
627.
3040.
627.
627.
627.
627.
627.
627.
627.
627.
627.
627.
]040.
627.
3040.
627.
627.
627.
3040.
627.
301,0.
]01,0.
III
U/
UI
U/
lI/
U/
JI
UI
U/
UI
II/
lI/
UI
II/
II/
III
U/
U/,
U/
U/
U/
U/
U/
III
U/
U/
III
U/
III
II/
III
U/
U/
UI
III
III
III
-------
ANALYTICAL DATA REPORT Z
Woodstock Landfill R "'S
Woodstock, Illinois
Hatrlx: SD Type: SVOC
Par_ter WK-S005-01 09/06/90 UK-SD06-01 09/06/90 UK-SD07-01 09/06/90 UK-SD08-01 09/06/90
.............. .........-.. --.""""'''''''' ............... --.....-.............. ....------..---..........--.-.. -...---.....-..------------ -.-.a_..__..... ...-..... -...... --...-
Phenol (UG/KG) 759. U/ 726. U/ ~29. U/ 1392. U/
bls(2-Chloroethyl) ether (UG/KG) 759. U/ 726. U/ 429. U/ 1392. U/
2-Chlorophenol (UG/KG) 759. U/ 7Z6. U/ 429. U/ 139Z- U/
',3-0Ichlorobenzene (UG/KG) 759. U/ 726. U/ ~29. U/ 1392. U/
',~-Olchlorobenzene (UG/KG) 759. U/ 726. U/ 429. U/ 1392. U/
Benzyl Alcohol (UG/KG) 759. II/ 726. U/ 429. U/ 1392. U/
1,2-Dlchlorobenzene (UG/KG) 759. U/ 7Z6. U/ 429. U/ 1392. U/
2-Hethylphenol (UG/KG) 759. U/ 726. U/ 429. U/ 1392. U/
bI8(2-Chlorolsopropyl)ether (UG/KG) 759. U/ 7Z6. U/ 429. U/ 1392. U/
4-Hethylphenol (UG/KG) 759. U/ 7Z6. U/ 429. U/ 1392. U/
N-Nltr~so'dl'n-dlpropylamlne (UG/KG) 759. II/ 726. U/ ~29. U/ 1392. U/
Hexachloroethane (UG/KG) 759. U/ 726. U/ ~29- U/ 1392. U/
Nitrobenzene (UG/KG) 759. U/ 126. U/ 429. U/ 1392. U/
Ilophorone (UG/KG) 759. U/ 726. U/ 429. U/ 7392. U/
2-Nltrophenol (UG/KG) 759. U/ 726. U/ 429. U/ 7392. U/
2,4-0lmethylphenol (UG/kG) 759. U/ 726. U/ 429. U/ 7392. U/
Benzoic Acid (UG/KG) 3680. u/ ]520. U/ 2080. U/ 35840. U/
bls(2-Chloroethoxy)methene WG/KG) 759. U/ 726, U/ 429. U/ 7392. U/
2,~-Olchlorophenol (UG/KG) 759. U/ 726. U/ ~29. U/ 7392. II/
',2,4-Trlchlorobenzene (UG/kG) 759. U/ 726. U/ 429. U/ 1392. U/
Naphthalene (UG/KG) 759. U/ 726. U/ 429. U/ 1392. U/
~-Chioroaniline (UG/KG) 759. U/ 726. U/ ~29. U/ 7392. U/
Hexachlorobutadlene (UG/KG) 759. U/ 726. U/ ~29. U/ 1392. U/
4-Chloro-3-methylphenol (UG/KG) 759. U/ 726. U/ 429. U/ 1392. U/
2-Hethylnlphthalene (UG/KG) 759. U/ 726. U/ 429. U/ 7392. U/
HeJlachlorocyclopentadlene (UG/Kfo) 759. U/ 726. U/ ~29. U/ 7392. U/
2,~,6-Trlchlorophenol (UG/KG) 759. U/ 726- U/ 429- U/ 1392- U/
2,~,5-'rlchlorophenol (UG/kG) 3680. U/ 3520. U/ 2080. U/ 358~0. U/
2-Chloronaphthalene (UG/KG) 759. U/ 726. U/ 429. U/ 1392. U/
2-Nltroanlllne (UG/KG) 3680. U/ ]5Z0. U/ 2080. U/ ]5840. U/
Olmethylphthalate (UG/KG) 759. U/ 726. UI 429. U/ 7392. U/
Acenaphthylene (UG/KG) 759. U/ 726. U/ ~29. U/ 7392. U/
2,6-0lnltrotoluene (UG/KG) 759. U/ 726. U/ ~29. U/ 7392. U/
3-Nltroanlllne (UG/KG) 3680. U/ 3520. U/ 2080. U/ 35840. u/
Acenlphthene (lIG/KG) 759. II/ 726. U/ 429. U/ 7J9Z. U/
2.4-0Inltrophenol (UG/KG) ]680. U/ ]520. U/ 2080. U/ ]5840. U/
4-Nltrophenol (UG/KG) ]680. u/ 3520. U/ 2080. u/ 35840. U/
Note: (I) Results are reported with qualifiers (Laboratory Quallfler/Oata Validation Qualifier) to the right of the value.
, "
II,
-------
ANALYTICAL DATA REPORT J
Uoodstock lendflll RllfS
Uoodstock, Illinois
Matrix: SO Type: SVOC
Parameter UK-SOOI-OI 09/06/90 UK-SOOI-91 09/06/90 UK.S002-01 09/06190 UK-S003-01 09/06/90 UK-SOOI,-OI 09/06190
._...-....--.. -......... .....---................. ............ ...... ........ .. .......... .... ...... --------..----....-....----- -------- ---. ......-- -- ----- ............................ ............ .. .. .... --........-..-...................----
Olbenzofuran (UG/KG) 1089. U/ 1188. U/ 1098.9 U/ 11,85. U/ 627. U/
2,4.0Inltrotoluene (UG/KG) 1089. U/ 1188. U/ 1098.9 U/ 11,85. U/ 627. U/
Olethylphthalate (UG/KG) 1089. U/ 1188. U/ 1098.9 U/ 11,85. U/ 627. U/
4.Chlorophenyl-phenylether (UG/ICG) 1089. U/ 1188. U/ 1098.9 UI 11,85. U/ 627. U/
fluorene (UG/KG) 1089. UI 1188. U/ 1098.9 UI 11,85. U/ 627. U/
4.Wltroanlllne (UG/KG) 5280. U/ 5760. U/ 5328. U/ 7200. U/ 3040. U/
4,6-0Inltro.2.methylphenol (UG/KG) 5280. U/ 5760. U/ 5328. UI 7200. U/ JOI,O. U/
N'nltrosodiphenylamlne (UG/KG) 1089. U/ 1188. U/ 1098.9 U/ 11,85. U/ 6?7. U/
'-Bromophenyl.phenylether (UG/KG) 1089. U/ 1188. U/ 1098.9 U/ 1485. U/ 627. UI
Nexachlorobenzene (UG/KG) 1089. UI 1188. U/ 1098.9 UI 148'). UI 627. UI
Pentachlorophenol (UG/KG) 5280. U/ 5760. U/ 5328. UI noo. U/ 301,0. UI
Phenanthrene (UG/KG) 1089. U/ 1188. U/ 1098.9 UI 11,85. UI 627. UI
Anthracene (UG/KG) 1089. U/ 1188. U/ 1098.9 UI 1485. U/ 627. III
Ol-n-butylphthalate (UG/KG) 1089. UI 1188. U/ 1098.9 U/ 11,8'). UI 627. UI
fluoranthene (UG/KG) 1089. U/ 1188. U/ 120. J/ 11,85. UI 627. UI
pyrene (UG/KG) 1089. U/ 1188. U/ 1098.9 U/ 11,85. UI 627. U/
Butylbenzylphthalate (UG/KG) 1089. U/ 1188. U/ 1098.9 U/ "85. U/ 627. UI
3,3'-Olchlorobenzldine (UG/KG) 2571,. U/ 21108. U/ 2597.' U/ 3510. U/ 1482. U/
BenZo(e)enthracene (UG/KG) 1089. UI 1188. U/ 1098.9 UI 11,85. UI 627. U/
Chrysene (UG/KG) 1089. U/ 1188. U/ 1098.9 U/ 1l,115. U/ 6?7. U/
bls(2'ethylhexyl)phthalate (UG/KG) 350. JI 250. J/ 1200. / 27n. JI 290. JI
Ol-n-octyl Phthalate (UG/KG) 1089. UI 1188. U/ 1098.9 UI 11,85. UI 627. UI
Benzo(b)fluoranthene (UG/KG) 1089. U/ 1188. U/ 1098.9 U/ 11,85. UI 627. UI
Benzo(k)fluoranthene (UG/KG) 1089. UI 1188. U/ 1098.9 UI 11,85. U/ 627. UI
Benzo(a)pyrene (UC/KG) 1089. UI 1188. U/ 1098.9 U/ 11,85. UI 627. UI
Indeno(I,2,3.cd)pyrene (UG/KG) 1089. U/ 1188. U/ 1098.9 UI 1485. UI 627. UI
Dlbenz(e,h)enthrecene (UG/KG) 1089. U/ 1188. U/ 1098.9 U/ 1485. U/ 627. UI
Benzo(g,h,l)perylene (UG/KG) 1089. UI 1188. U/ 1098.9 UI 1485. UI 627. UI
Note: (1) Results ore reported with qualifiers (laboratory Qualifier/Data Validation Qualifier) to the right of the value.
. 'I
" .
-------
. 01 " )
ANALYf.CAL DAfA REPORf 4
Uoodstock Landlill RI/fS
Uoodstock, '1llnols
Hatrix: SD fype: SVOC
Parameter UK-SD05-0! 09106/90 UK-SD06-01 09/06190 UK-SD07'0! 09/06190 UK-S008-01 09106190
-............... ................................ ..-.... .................. -... ......... ......... .-----.-..-..........-........-..-.. -.....-......---................-- ----.......------......-------
Dlbenzoluran (UG/KG) 759. U/ 726. UI 429. UI 7J92. UI
2,4-0Inltrotoluene (UG/KG) 759. UI 726. U/ 429. U/ 7J92. UI
Dlethylphthalate (UG/KG) 759. U/ 726. UI 429. U/ 7J92. UI
4-Chlorophenyl'phenylether (UG/KG) 759. U/ 726. U/ 429. U/ 7J92. UI
Fluorene (UG/KG) 759. UI 726. U/ 429. U/ 7J92- UI
4-Nltroanillne (UG/KG) 3680. U/ 3520. U/ 2080. U/ 35840. UI
4,6-Dlnitro-2-methylphenol (UG/KG) 3680. UI 3520. U/ 2080. UI 35640. U/
N-nltroSodiphenylamine (UG/KG) 759. U/ 726. U/ 429. U/ 7392. UI
4-Bromophenyl-phenylether (UG/Ke) 759. U/ 726. U/ 429. U/ 7392. U/
Hexachlorobenzene (UG/KG) 759. UI 726. U/ 429. U/ 7392. U/
Pentachlorophenol (UG/Ke) 3680. U/ 3520. U/ 2080. U/ 35640. U/
Phenanthrene (Ue/KG) 759. U/ 726. U/ 429. UI 7392. UI
Anthracene (UG/KG) 759. UI 726. UI 429. UI n92. UI
DI-n-butylphthalate (UG/Ke) 759. U/ 726. U/ 429. U/ 7392. U/
Ftuoranthene (UG/KG) 759. U/ 726. U/ 429. U/ 7392. U/
Pyrene CUG/KG) 759. U/ 726. U/ 429. U/ 7392. U/
Butytbenzylphthatate (UG/Ke) 759. U/ 726. UI 429. U/ 7392. U/
3,3'-Olchlorobenzldine (Ue/KG) 1794. U/ 1716. U/ 1014. UI 17472. UI
Benzo(a)anthracene (UG/KG) 759. u/ 726. U/ 429. U/ 7392. U/
Chrysene (UG/KG) 759. U/ 726. U/ 429. U/ 7392. U/
bls(~-ethylhexyl)phthalate (Ue/Ke) 220. J/ 200. J/ 60. JI 7392. U/
Dt-n-octyt Phthatate (UG/KG) 759. U/ 726. U/ 429. U/ 7392. U/
Benzo(b)Ituoranthene (UG/KG) 759. U/ 726. U/ 429. U/ 7392. U/
Benzo(k)Ituoranthene (UG/KG) 759. U/ 726. U/ 429. U/ 7392. U/
Benzo(a)pyrene (Ue/KG) 759. U/ 726. U/ 429. U/ 7392. UI
Indeno(I,2,3-cd)pyrene (UG/Ke) 759. U/ 726. U/ 429. U/ 7392. U/
Dlbenz(a,h)anthracene (UG/KG) 759. U/ 726. U/ 429. U/ 7392. U/
Benzo(g,h,l)perytene (UG/KG) 759. U/ 726. U/ 429. U/ 7392- U/
Note: (1) Results ore reported with quoliliers (lnhorotory Ouolilier/Oata Validotlon Ouolifier) to the right of the volue.
-------
ANALYTICAL DATA REPORT
~oodstock Land'ill RIIFS
~oodstock, Illinois
HatriK: SO Type: PPCB
Generated by: CA~
Date Issued: 10-HAY-91
Parameter WK.SDDI-01 09/06/90 ~K-SOOI-91 09/06/90 ~-S002-01 09/06/90 ~-SoOJ'OI 09/06/90 UK-SOO'.OI 09/06/90
~..--------------------------- ~_..-------------------- ---------------..-------- ...-----.............. -- --...... --.. ............................ .. .. .. .............. .................. .. .. .. .. .. .. .. .. .. .. .... .. .. ..
alpha.BIIC (IIG/KG) 28. III 28. UI 28. III J60. UI 1600. UI
beU-BHC (IIG/k'G) 28. III 28. UI 28. UI J60. UI 1600. III
delta-BHC (IIG/KG) 28. III 28. UI 28. III J60. III 1600. III
gamma-BHC (Lindane) (IIG/KG) 28. III 28. UI 28. III 360. UI 1600. III
Heptachlor (UG/KG) 28. UI 28. UI 28. UI 360. UI 1600. UI
Aldrin (UG/KG) 28. UI 28. UI 28. UI 360. UI 1600. UI
Heptachlor epoKlde (IIG/k'G) 28. III 28. UI 28. UI 360. UI 1600. UI
fndosul'an I (UG/k'G) 28. ul 28. UI 28. III 360. UI 1600. III
Dieldrin (UG/KG) 56. UI 56. UI 56. UI 110. UI 3100. UI
1"I,I-DOf (UG/KG) 56. III 56. UI 56. III 710. UI ]100. IJI
fndrln (UG/KG) 56. III 56. UI 56. III 710. UI 3100. III
fndosulfan II (IIG/KG) 56. UI 56. UI 56. UI 710. UI 3100. III
1,,1,'-000 (UG/KG) 56. UI 56. UI 56. III 110. III 3100. III
fndosulfan sulfate (UG/KG) 56. UI 56. UI 56. UI 710. UI 3100. III
',"-OOT (UG/I(G) 56. III 56. U/ 56. UI 710. II/ 3100. III
HethoKychlor (UG/KG) 280. UI 280. UI 280. UI 3600. U/ 16000. U/
fndrln ketone (UG/KG) 56. U/ 56. U/ 56. U/ 710. U/ 3100. III
alpha-Chlordane (UG/KG) 280-. U/ 280. U/ 280. U/ 3600. U/ 16000. III
gamma-Chlordane (UG/KG) 280. U/ 280. U/ 280. U/ 3600. U/ 16000. U/
TOKaphene (UG/"G) 560. UI 560. U/ 560. U/ 1100. U/ ]1000. U/
Aroclor-1016 (UG/KG) 280. U/ 280. U/ 280. U/ 3600. U/ 16000. U/
Aroclor-1221 (UG/KG) 280. U/ 280. U/ 280. U/ 3600. u/ 16000. II/
Aroclor.1232 (UG/KG) 280. U/ 280. U/ 280. U/ 3600. U/ 16000. II/
Aroclor-12'2 (UG/KG) 280. U/ 280. U/ 280. U/ 3600. UI 16000. UI
Aroclor-12'8 (UG/"G) 280. UI 280. U/ 280. U/ ]600. U/ 16000. III
Aroclor-125' (UG/"G) 560. II/ 560. U/ 560. U/ .'1100. u/ 31000. U/
Aroc!or-1260 (UG/KG)" 560. U/ 560. U/ 560. UI 7100. UI 31000. UI
Note: (1) Results ere reported with qualifiers (lahoratory Qualifier/Oata validation Qualifier) to the right 0' the value.
, ; I
" 0
-------
. .'
'. :;
ANAlYfIUI. PArA RfPORr 2
Uoodstock I.andlill RI/fS
UOodstock, Illinois
Matrix: 50 Type: PPCB
Parameter UK-SOOS-OI 09/06/90 UK-S006-01 09/06/90 UK-S007-01 09/06/90 UK-S008-01 09/06/90
........................... .. .. .. .. ............ .................. .....----... --... --........--- -... -........ ......-......... --.. ---........ ..................................... .. .. .. ........ .. -- ....-...... ........... -.........---..
alpha-8HC (UG/KG) 19. U/ 18. U/ 10. U/ 60. U/
beta-8HC (UG/KG) 19. U/ 18. U/ 10. U/ 60. U/
delta-8HC (UG/KG) 19. U/ 18. U/ 10. U/ 60. U/
9amna-BIIC (lindane) CUG/KG) 19. U/ 18. II/ 10. II/ 60. II/
Heptachlor (UG/KG) 19. U/ 18. U/ 10. U/ 60. U/
Aldrin CUG/KG) 19. U/ 18. U/ 10. U/ 60. U/
Heptachlor epoxlde (UG/KG) 19. U/ 18. U/ 10. U/ 60. U/
Endosulfen I (UG/KG) 19. U/ 18. U/ 10. U/ 60. U/
DIeldrin (UG/KG) 38. U/ 36. U/ 20. U/ 120. U/
4,4' -ODE (UG/KG) 38. U/ 36. U/ 20. U/ 120. U/
Endrln (UG/ICG) 38. U/ 36. U/ 20. U/ 120. U/
Endosulfan II (UG/KG) 38. U/ 36. U/ 20. II/ 120. II/
4,4'-000 (UG/KG) 38. II/ 36. U/ 20. U/ 120. U/
Endosulfan sulfate (UG/KG) 38. u/ 36. U/ 20. U/ 120. U/
4,4"00r (UG/KG) 38. U/ 36. U/ 20. U/ 120. U/
Methoxychlor (UG/KG) 190. U/ 180. U/ 100. II/ 600. II/
Endrln ketone (UG/KG) 38. U/ 36. u/ 20. U/ 120. II/
alpha-Chlordane (UG/KG) 190. U/ 180. U/ 100. U/ 600. U/
gamma-Chlordane (UG/KG) 190. U/ 180. U/ 100. U/ 600. U/
Toxaphene (UG/ICG) 380. U/ 360. U/ 200. U/ 1200. u/
Aroclor-1016 (UG/ICG) 190. U/ 180. U/ 100. U/ 600. U/
AroClor-1221 (UG/ICG) 190. U/ 180. U/ 100. II/ 600. U/
Aroclor'1232 (UG/KG) 190. U/ 180. II/ 100. U/ 600- u/
Aroclor-1242 (UG/kG) 190. II/ 180. U/ 100. U/ 600. u/
Aroclor-1248 (UG/kG) 190. II/ 180. U/ 100. U/ 600. U/
Aroclor-1254 (UG/ICG) 380. II/ 360. U/ 200. U/ 1200. U/
Aroclor-1260 (UG/ICG) 380. II/ 360. II/ 200. U/ 1200. II/
Note: (n Results ore reported with qunlifie,'s (lohoratory Qualifier/Data Validation Qualifier) to Ihe right 01 Ihe value.
-------
SUMMARY OF TENTATIVELY IDENTIFIED COMPOUNDS
Woodstock landfill RI/FS
wooastocic. III inois
Matrix: SD
Generate: by; CAW
Date Issued: 10-MAY-91
wr::-S:>01-01
09/06/90
(T8NA) Tentatively-Identified Semi-VolatiLes
C~und CUnitS)
........-.....-....--.-.-.....-.-.-.-----.-
Unknown CUG/KG)
AldoL (UG/KG)
Aldol (UG/KG)
Aldol (UG/KG)
Unknown hydrocarbon (UG/KG)
Unknown hydrocarbon (UG/KG)
9-0ctadecene. (E)- (UG/KG)
Unknown hydrocarbon (UG/KG)
Unicnown hydrocarbon (UG/KG)
Unknown (UG/KG)
Unknown hydrocarbon CUG/KG)
Heptadecane, 2.6-dimethyl- (UG/KG)
9.0ctadecene, (E)- (UG/KG)
Unknown hydrocarbon (UG/KG)
Tetracontane. 3.5,24-trimethyl CUG/KG)
Unknown hydrocarbon (UG/KG)
Unknown (UG/KG)
Unknown CUG/KG)
Unknown (UG/ICG)
Unknown (UG/ICG)
Unknown (UG/ICG)
Unknown (UG/ICG)
Concentration
LQ/DVQ
---..--..---------------.------.
3800.
2800.
700.
700.
2000.
930.
2600.
460.
350.
'400.
2000.
2600.
7100.
1500.
3000.
1600.
1400.
8'0.
1000.
1500.
930.
930.
J/
AJ/
AJ/
AJ/
J/
J/
J/
j/
J/
J/
J/
J/
J/
J/
J/
J/
J/
J/
J/
J/
J/
J/
-------
Matrix: SO
IJK-S001 -91
09/06/90
(TBNA) T~ntativ~ly.ldentified Semi-Volatiles
C~ (Units)
SUMMARY OF TENTATIVELY IDENTIFIEO COMPOUNDS
Woodstock Landfill RI/FS
Woodstock, Illinois
-........-..-..........................-...
Concentration
-.-.........---.-.-.-------....-
LQIOVQ
Aldol (UG/ICG)
Aldol (UG/ICG)
Unknown (UG/ICG)
Tribromo~enol (UG/ICG)
'-Heptadecanol (UG/ICG)
Unknown hydrocarbon (UG/ICG)
Unknown hydrocarbon CUG/ICG)
Unknown hydrocarbon (UG/ICG)
Unknown hydrocarbon CUG/ICG)
Unknown hydrocarbon CUG/ICG)
Unknown hydrocarbon CUG/ICG)
Unknown hydrocarbon (UG/ICG)
Unknown hydrocarbon- (UG/ICG)
Unknown hydrocarbon (UG/ICG)
Iron, tricarbony![N-(phenyl-
Unknown hydrocarbon CUG/ICG)
Unknown hydrocarbon CUG/ICG)
Unknown hydrocarbon CUG/KG)
Pentacosane CUG/ICG)
Unknown hydrocarbon
Unknown hydrocarbon
Unknown hydrocarbon
(UG/ICG)
CUG/ICG)
CUG/ICG)
CUG/ICG)
2900.
2700.
2800.
1300.
'1.00.
'1.00.
'600.
1.1.00.
2100.
'200.
5900.
1300.
1600.
2300.
1.100.
6500.
2300.
2'-00.
3800.
3600.
2200.
5700.
2
AJ/
AJ/
J/
J/
J/
J/
J/
J/
J/
J/
J/
J/
J/
J/
J/
JI
JI
J/
J/
J/
J/
J/
-------
Matr; x: SO
IIK-5002.01
SUMMARY OF TENTATIVELY IDENTIFIED COMPOUNDS
lloodstock Landfill RI/FS
lloodstock, Illinois
3
09/06/90
(TBNA) Tentatively' Identified Semi-Volatiles
LQ/DVQ
C~und (Units)
Concentration
........-------.-----------------------.--.
---.----------------------------
Unknown (UG/KG) 1200. J/
Aldol (UG/KG) 6100. AJ/
Aldol (UG/KG) 4100. AJ/
Aldol (UG/KG) 700. AJ/
Unknown subst. hydrocarbon (UG/ICG) 1600. J/
Unknown hydrocarbon (UG/KG) 1500. JI
Unknown hydrocarbon (UG/KG) 5100. J/
Unknown hydrocarbon (UG/KG) 1000. J/
Unknown hydrocarbon (UG/KG) 3600. J/
Unknown (UG/KG) 930. J/
Unknown hydrocarbon (UG/KG) 1200. J/
Unknown hydrocarbon (UG/KG) 2300. J/
Unknown hydrocarbon (UC/KG) 1,"00. J/
Pentacosane (UG/KG) 1600. J/
Unknown hydrocarbon (UG/KG) 2600. J/
Unknown (UG/ICG) 3000. J/
Unknown hydrocarbon CUG/KG) 3500. J/
Pentacosane (UG/KG) 6900. J/
Unknown hydrocarbon (UG/KG) 12000. J/
Pentacosane (UG/KG) 12000. J/
Unknown (UG/ICG) 5,"00. J/
Unknown (UG/KG) 7700. J/
Unknown (UG/KG) 13000. J/
-------
SUMMARr OF TENTATIVELY IDENTIFIED COMPOUNDS
Woodstock Landfill RI/FS
WoOdstock, Illinois
Ma:rix: SD
'-':'S003.01
09/06/90
(TBNA) Tentatively.Identified Semi.Volatiles
Compound (Units)
Concentration
-....--...........---...........
LQ/DW
...........................................
Unknown (UG/ICG)
Aldol (UG/ICG)
Aldol (UG/ICG)
Aldol (UG/ICG)
Unknown (UG/ICG)
Oimethylheptadecane (UG/ICG)
Hexanedioic acid, mono(2'ethyl
Dimethylheptadecane (UG/ICG)
Oimethylheptadecane (UG/ICG)
Unknown (UG/ICG)
Unknown (UG/ICG)
Unknown (UG/ICG)
Unknown (UG/ICG)
Oimethylheptadecane (UG/ICG)
Unknown (UG/ICG)
Unknown (UG/JC:G)
Unknown (UG/JC:G)
Unknown (UG/ICG)
Octacosane (UG/ICG)
Unknown (UG/ICG)
Unknown (UG/ICG)
(UG/ICG)
1300.
6500.
2500.
3100.
1500.
890.
7100.
1200.
1600.
890.
2700.
1300.
'500.
10600.
1800.
6l.00.
890.
2800.
1800.
1500.
21000.
,
JI
AJ/
AJ/
AJ/
JI
JI
J/
JI
JI
JI
JI
JI
JI
JI
JI
JI
JI
JI
JI
JI
JI
-------
Matri~: SO
IJI(-SOOI.-01
SUMMARY OF TENTATIVELY 10ENTIFIEO COMPOUNOS
Woodstock landfill RI/FS
Woodstock, Illinois
09/06/90
(TBNA) Tentatively-Identified Semi-volatiles
C~ (Units)
Concentrat i on
le/ove
WIC-S005-01
-----.------.-.--.-....-.-.....-.---.-.....
-...---...-.---------.-.-.----.-
Aldol (UG/ICG)
A ldo l (UG/ICG)
Aldol (UG/ICG)
Heptadecane (UG/ICG)
Sulfur + unknown (UG/ICG)
unknown hydrocarbon (UG/ICG)
Hexanedioic acid, mono(2-ethyl
Oimethylheptadecane (UG/ICG)
Unknown (UG/KG)
Unknown hydrocarbon (UG/ICG)
Unknown (UG/ICG)
Unknown (UG/ICG)
Unknown (UG/ICG)
Unknown hydrocarbon (UG/ICG)
Unknown (UG/ICG)
Unknown (UG/ICG)
Unknown (UG/ICG)
Unknown CUG/ICG)
Oimethylheptadecane (UG/ICG)
Unknown (UG/ICG)
Unknown CUG/KG)
Unknown (UG/ICG)
Unknown (UG/ICG)
1300.
2300.
1,60-
650.
10000.
330-
390.
520.
330.
2000.
650.
650.
5500.
3700.
2300.
9'0.
3100.
'200.
850.
1300.
1200.
2300.
1000.
AJ/
AJ/
AJ/
J/
J/
JI
J/
J/
J/
JI
J/
J/
J/
J/
J/
J/
J/
J/
J/
J/
J/
J/
J/
(UG/ICG)
09/06/90
(TBNA) Tentatively-Identified Semi-Volatiles
le/Ove
CQII1X)und (Uni ts)
Concentrat ion
.-------------.-...-..----.-.-.-.-.-.-.-.-.
---.-.---.-.-.-------.-.----.-.-
Unknown (UG/ICG)
Aldol (UG/I:G)
A ldo l (UG/ICG)
Unknown (UG/ICG)
Unknown CUG/ICG)
Unknown CUG/ICG)
Unknown CUG/ICG)
Unknown CUG/ICG)
Dimethylheptadecane (UG/ICC)
2200. JI
1500. AJ/
1':'00. AJ/
2000. J/
690. J/
390. J/
310. JI
1060. J/
770. J/
-------
6
SU~MARY OF ~EN~A~IVElY 10ENTIFIEO C~POUMOS
wooCstOCk Landfill RI/FS
woodstOCk, Illinois
!'\at~~X: SO
W(.S006-01
09/06/90
(T6NA) Tentatively-Identified semi-volatiles
compound (units)
-....--...---------------------..--..------
Aldol (UG/(G)
Aldol (UG/(G)
Aldol (UG/(G)
Fluorophenol (UG/KG)
Unknown (UG/KG)
Unknown hydrocarbon (UG/KG)
Unknown (UG/KG)
Unknown aldehyde (UG/KG)
Unknown hydrocarbon (UG/KG)
unknown (UG/ICG)
Unknown (UG/KG)
Unknown aldehyde (UG/ICG)
unknOwn hydrocarbon (UG/ICG)
unknown (UG/ICG)
Unknown (UG/ICG)
Unknown aldehyde (UG/ICG)
Unknown hydrocarbOn (UG/ICG)
Unknown (UG/KG)
vitamin E acetate + unknown (UG/KG)
Unknown aldehyde (UG/KG)
unknown (UG/ICG)
Unknown (UG/KG)
Unkno..'" -.~G)
concentrat i on
-.-.....-.--.-.-----....--------
LQ/OVCI
1200.
11,00.
370.
600.
370.
300.
1200.
370.
670.
1800.
890.
3200.
1900.
71.00.
520.
1700.
1500.
1900.
890.
820.
1800.
890.
1900.
AJ/
AJ/
AJ/
J/
J/
J/
J/
J/
J/
J/
J/
J/
J/
J/
J/
J/
J/
J/
J/
J/
J/
J/
J/
-
-------
Matrix: S;)
II1(-S007-01
SUMMARY OF TEHTATIVELY IDENTIFIED COMPOUNDS
woodstock Landfill RI/FS.
woodstock, Illinois
09/06/90
(iBNA) Tentatively-Identified Semi-Volatiles
COII'OOur.Q (Units)
II1(-SDD13.D1
.----------..------------------------------
Aldol (UG/KG)
Aldol (UG/ICG)
Aldol (UG/KG)
Aldol (UG/ICG)
Aldol (UG/ICG)
1-0ecanol, ,-ethyl-
17-Pentatriacontene
Unknown hydrocarbon
Unknown (UG/ICG)
Unknown hydrocarbon (UG/ICG)
Oodecane, 1.iodo- (UG/KG)
Unknown hydrocarbon (UG/ICG)
Unknown hydrocarbon (UG/KG)
Unknown (UG/KG)
Unknown hydrocarbon (UG/ICG)
Unknown hydrocarbon (UG/ICG)
Unknown hydrocarbon (UG/KG)
Unknown (UG/KG)
Unknown (UG/ICG)
(UG/ICG)
(UG/KG)
(UG/KG)
09/06/90
(TBHA) Tentatively-Identified Semi-Volatiles
C~ (Units)
'.
------------------------------.----------.-
Aldol (UG/ICG)
Heptadecane, 2,6-dimethyl- (UG/ICG)
Unknown hydrocarbon (UG/ICG)
Unknown (UG/ICG)
Unknown hydrocarbon (UG/KG)
Heptadecane, 2,6-dimethyl- (UG/ICG)
Unknown hydrocarbon (UG/ICG)
Unknown hydrocarbon (UG/KG)
Octacosane (UGltG)
Vitamin E acetate (VAH) (UG/KG)
Unknown hydrocarbon (UG/ICG)
Unknown hydrocarbon (UG/ICG)
Unknown (UG/ICG)
Unknown (UG/KG)
.
.
Conc:entration
7
----...---------.-------------.-
LQ/DVQ
BOD.
730.
3/.0.
210.
510.
"3D-
730.
170.
170.
390-
560.
1200.
300.
510.
210.
/'300.
300.
300.
1800.
Concentration
AJ/
AJ/
AJ/
AJ/
AJ/
JI
J/
J/
J/
J/
J/
J/
J/
J/
J/
J/
JI
J/
J/
--------------------------------
LQ/DVQ
1"000.
/'500.
/'500.
5200.
6000.
37000.
20000.
3000.
16000.
19000.
13000.
9000.
8200.
513000.
AJ/
J/
J/
J/
J/
J/
J/
J/
J/
J/
J/
J/
J/
J/
-------
SURFACE WATER
-------
. I
t. :
ANAlY'ICAl DA'A REPOR'
Uoodstock land'III RIIFS
Uoodstock, illinois
Hatrilc: SU 'ype: IND HIl
Generated by: CAU
oete Issued: 10-HAY-91
Peremeter UK.SW01-01 11/20/90 UK-SU01-91 11/20/90 UK.SU10.01 0'/02/91 UK-SU10-91 0'/02/91 ur.SV"-0' 0'/03/91
........--......... .......... -.. .a__- ..........-.......... ........ ............ ..................--------....---- ---.. ...--.....",.. .......-.. --......... -..-----------..--------.. -......_.._-------.-.-_....
Ah..lnun (UG/l) 50. UI 50. UI 16. '1.1 113.5 '1.1 81. '1.1
Ant llIIOnY (UG/l) 50. UI 50. UI 50. UI 50. UI 50. UI
Arsenic (UG/l) 2.4 KNS/J 2. UN/UJ 2. UI 2. UI 2. UI
..rlUli (UG/l) 222. I 195. '1.1 '8.5 '1.1 '8. '1.1 61.5 '1.1
leryilium (UG/L) 5. UI 5. UI 5. UI 5. UI 5. UI
ClKhh... (UG/L) 5. UI 5. U/ 5. U/ 5. UI 5. ul
Ce'clUli (UG/l) 199000- I 189000. I 19000. I 79600. I 86100. I
ChrOllllum, totel (UG/l) 10. UI 10. U/ 10. UI 10. UI 10. UI
Cobalt (UGIl) 10. . UI 10. U/ 10. UI 10. UI 10. UI
Copper (UG/l) 1'. '1.1 12. '1.1 10. UI 10. UI 10. UI
Iron (UG/l) 32200. I 28000. I 432. I 396. / 1190. I
leed (UG/l) 1,.6 S*/J 5.3 S*/J 3. UI ]. UI ]. UI
Megneslum (UG/l) 126000. I 126000. I ]1600. 1 31000. I 1,6300. I
Mentenese (UG/l) 615. I 641. I 54.5 I 52. I 86.5 I
Mercury (UG/l) 0.2 UI 0.2 U/ 0.2 UI 0.2 UI 0.2 UI
Nickel (UG/l) 121. I 141. I 20. UI 20. UI 20. UI
potesllum (UG/l) 16000. I 15700. / 1220. '1.1 1220. '1.1 10100. I
SelenlUli (UG/l) 2. UI 2. USI 2. UI 2. UI 2. UI
Sliver (UG/l) 10. UI 10. U/ 10. UI 10. UI 10. UI
SodlUli (UG/l) 631,00. I 601,00. I 28900. I ]0200. I 35100. I
lhel'IUli (UG/l) ]. UI ]. UI ]. UI ]. UI 3. UI
Ven.dlu. (UG/l) 50. UI 50. U/ 50. UI 50. UI 50. UI
Zinc (UC/l) 264. I 225. I 10. UI 10. UI 181. I
Cyenlde (UG/l) 10. UI 10. UI
Alk.tlnlty, lot., (HG/l) 234. / 23'. I 368. I
Chloride (MG/l) 10. I 69. I 67. I
NltretetNltrite Nitrogen (HG/l) 4.]] I '.23 I J.2 I
Nitrogen, A~le (HG/l) 0.21 I 0.24 I 1.51 I
Nitrogen, lotel 'I.Jeldahl (HG/l) 1.82 N/J 1.93 N/J ].411 N/J
Phosphoru), 'otal (HG/l) 0.03 / 0.03 I 0.01, I
Sui 'ate (MG/l) 74. / 61. I 10. I
'otal Dissolved Solids (HG/l) 506. I 1.18. I 600. I
Note: (I> Results nre reported with qunlifiers (Iahoratory Qualifler/Data Validation Quellfler) to the right of the \/81I1e.
-------
H.trh: 511
l'(pe: INO
Hfl
ANALYIICAL OAIA .(POR'
VOGdttock lIIrdrt II .1/1$
UGOdstock, Illinois
I
'.r_t,r Uk-SUI1-01 "/OJ191 Uk'SUIIOI.OI 11/20/90 Uk-SUI'10-01 0"0)/91
................ ..-.....-... -.. - -. --- .-..----.............---- ..-..---..........--........ ....... -........ --..-...................-
A h..l,..ft (UG/L) 89. rl 50. UI 50. UI
Ant I.."..y (UG/l) 50. UI 50. UI 50. UI
Are'nlc (UG/l) I. UI 2. "'IU.I 2. UI
'.rlu. (UG/l) 13.5 KI 10. UI 10. UI
..ryillu. (UG/l) 5. UI 5. UI 5. UI
C"Iu. (UG/') 5. UI 5. UI 5. UI
[.Iclu. (UGIl) 99200. I 1000. UI 1000. UI
Chro.lu., to..1 (UG/') 10. UI 10. UI 10. UI
Colla I t (UG/l) 10. U/.. 10. UI 10. UI
. C.".,.r (UG/l) 10. UI 10. UI 10. UI
'rOft (UG/l) 9116. 1 20. UI 20. UI
had (UG/l) ). UI ). uelU.I 1. UI
M..,.IIu. (UG/l) 58100. I 1000. UI 1000. UI
Manoanel. (UG/l) 64. I 10. UI 10. UI
Mercury (UG/l) 0.2 UI 0.2 UI 0.2 UI
Ilchl (UG/l) 20. UI 20. KIU 20. UI
'ot...I", (UG/l) 9920. I 100. UI 100. UI
Sel anlu. (UGIl) 2. USI 2. UI 2. UI
I" var (UG/l) 10. UI 10. UI 10. UI
Sodl", (UG/I) 18500. I 2000. UI 2000. UI
1".1' Iu. (UG/l) ). UI J. UI J. UI
Vanadlu. (UG/l) 50. U/ 50. UI 50. UI
line (UG/l) 90. I 10. UI 10. UI
Cyanide (UG/') 10. UI
A".llnlty, lot.1 (HGIl) '12. I 5. UI
[Illoride (HO/l) 64. I 1. UI
Illr.t..lltrlt. Iitrogen (HG/l) 2.51 I 0.02 UI
""IIIM, bIIIonl. (HO/l) 1.6 I 0.1 UI
IllrOl,n, lot.1 KJeldahl (HG/l) ].~, NO 0.1) II"
PholpllorUl, '0..1 (HG/l) 0.0' I 0.02 UI
Sulfet. (Nell) 69. I 5. UI
lotel OlssolYed Solids (HG/L) 652. I 20. UI
NOI': (1) ...,,,1 Is II'" report"d with <1',81 !li"rs (I llhoratory OU81111er/08" V.lld.tlon Gu811f1er) to the right 0' the Yllille.
I' ,
-------
, ,
t: '
HatrlK: SU Type: SVOC
Generated by: CAU
Dlte Issued: 10-HAY-91
Parameter
ANALYTICAL DATA REPORT
Uoodstock landfill RI/fS
Uoodstock, Illinois
.....................-..... ----.-........ .... .-..
VK-SVOI'OI 11/20/90
..----....-----------------
UK-SUFBOI.01 11/20/90
UK-SUOI-91 ',/20/90
........-..-..-----..---..........
Phenol (UG/l) '0.
bls(Z-Chloroethyl) ether (UG/l) '0.
2-Chlorophenol (UG/l) '0.
',J-Dlchlorobenzene (UG/l) '0.
',4-Dlchlorobenzene (UG/l) 10.
Benzyl Alcohol (UG/l) 10.
I,Z-Dlchlorobenzene (UG/l) 10.
2-Hethylphenol (UG/l) 10.
bll(Z'Chloroisopropyl)ether (UG/l) 10.
4'Hethylphenol (UG/l) 10.
N-Nltroso-dl'n-dlpropylamlne (UG/l) '0.
He.lchloroethlne (UG/l) 10.
NI trobenrene (IIG/l) 10.
Ilophorone (UG/l) 10.
2'Nltrophenol (UG/l) 10.
2,4-0lmethylphenol (UG/l) '0.
Benzoic Acid (UG/l) 50.
bls(Z-ChloroethoKy)methane (UG/l) 10.
2,4-0lchlorophenol (UG/l) 10.
1,2,4-Trlchlorobenzene (UG/l) 10.
Nlphthllene (UG/l) 10.
4-Chlorolnlllne (UG/l) 10.
HeMlchlorobutldlene (UG/l) 10.
4'Chloro-J-methylphenol (UG/l) 10.
2-Hethylnaphthelene (UG/l) 10.
HeKechlorocyclopentediene (UG/l) 10.
2,4,6-Trlchlorophenol (UG/l) 10.
2,4,5-Trlchlorophenol (UG/l) 50.
Z'Chloronaphthelene (UG/l) 10.
2-Nltroanlline (UG/l) 50.
Dlmethylphthalate (UG/l) 10.
Acenaphthylene (UG/l) 10.
2,6'Olnltrotoluene (UG/l) 10.
J.Nitroanlline (UG/l) 50.
Acenephthene (UG/L) 10.
2,4-0lnitrophenol (UG/L) 50.
'.N i t rophenol ClJG/l) 50.
Note: (1) Results lire reporterl with qualifiers
-..------ -------- -- -- -- -..
U/ 10. U/ 10.
U/ to. UI 10.
U/ '0. U/ '0.
U/ '0. U/ 10.
U/ to. UI '0.
U/ to. U/ '0.
U/ to. U/ 10.
U/ 10. UI 10.
U/ 10. U/ to.
U/ '0. U/ 10.
U/ 10. U/ 10.
U/ 10. U/ 10.
U/ 10. U/ 10.
U/ 10. U/ 10.
U/ to. U/ to.
U/ to. U/ 10.
U/ 50. U/ 50.
U/ to. U/ to.
U/ '0. U/ 10.
U/ 10. U/ to.
U/ to. U/ 10.
U/ 10. U/ to.
U/ to. U/ to.
U/ to. U/ to.
U/ to. U/ to.
U/ 10. U/ to.
U/ to. U/ to.
U/ 50. U/ 50.
U/ to. U/ to.
U/ 50. U/ 50.
UI 10. U/ 10.
U/ to. U/ to.
U/ 10. U/ 10.
III 50. U/ 50.
II/ 10. UI 10.
II/ 50. U/ 50.
II/ 50. U/ 50.
(loboratory Quallfier/Oeta Validation Qualifier) to
U/
U/
U/
U/
U/
U/
U/
U/
U/
U/
U/
U/
U/
II/
II/
U/
U/
U/
U/
U/
U/
U/
U/
U/
U/
U/
U/
U/
U/
U/
U/
U/
U/
U/
II/
II/
II/
the right
of the vel ue.
-------
ANALYTICAL DATA REPORT 2
uoodstock landfill RI/FS
Uoodstock, 1IIInol5
Matrix: SU Type: SVOC
Parameter UK-SUOI-OI 11/20190 UK-SUOI-91 11/20190 UK-SUFBOI-01 11/20190
...---.------.----------...--- -----.-...-------------- ----...-..---------------- ---............."''' ----.. ....-_......
Olbenlofuran (IIG/l) 10. UI 10. III 10. III
2,4-0Inltrotoluene (IIG/l) 10. UI 10. III 10. III
Olethylphthalate (IIG/l) 10. UI 10. UI 10. III
4-Chlorophenyl-phenylether (IIG/l) 10. UI 10. UI 10. III
Fluorene (IIG/l) 10. UI 10. III 10. III
4-Nltroanlllne (IIG/l) 50. UI 50. UI 50. III
4,6-0Inltro-Z-methylphenol (IIG/l) 50. UI 50. III 50. III
N.nltrosodlphenylamlne (UG/l) 10. UI 10. UI 10. III
4-Bromophenyl'phenylether (IIG/l) 10. U/ 10. III 10. III
Hexachlorobenzene (IIG/l) 10. U/ 10. III 10. UI
Pentachlorophenol (UG/l) 50. UI 50. UI 50. III
Phenenthrene (UG/L) 10. UI 10. III 10. III
Anthracene (HG/l) 10. U/ 1i1. UI 10. III
Ol-n-butylphthalate (IIG/l) 10. UI 10. III 10. III
Fluoranthene (IIG/l) 10. U/ 10. III 10. III
Pyrene (IIG/l) 10. U/ 10. III 10. UI
Butvlbenlylphthalete (IIG/l) 10. UI 10. UI 10. III
3,3"Olchtorobenzldlne (IIG/l) 20. U/ 20. III 20. III
Benlo(e)enthrecene (IIG/l) 10. UI 10. III 10. III
Chrysene (IIG/l) 10. UI 10. III 10. III
ble(2-ethylhexyl)phthelete (IIG/l) 24. B/IIJ 39. B/UJ 5. BJI
Ol-n-octyt Phthalate (IIG/l) 10. UI 10. UI 10. III
Benlo(b)fluorenthene (IIG/l) 10. UI 10. III 10. U/
Benzo(k)ftuorenthene (IIG/l) 10. U/ 10. III 10. III
Benlo(e)pyrene (IIG/l) 10. U/ 10. III 10. III
Indeno(1,2,3-cd)pyrene (IIG/l) 10. U/ 10. III 10. III
Olbenz(e,h)enthrecene (IIG/l) 10. UI 10. III 10. III
Benzo(g,h,l)perylene (IIG/l) 10. U/ 10. III 10. III
Note: (I) Results are reported with quo I ifier~ (I nboratory Quailfier/Data Validation Qualifier) to the right of the value.
,. .
-------
. ,
[ ~ :
ANALYTICAL DATA REPORT
Uoodstock landf i II RI/fS
Uoodstock, illinois
Hatrill: SU Type: vac
Generated by: CAU
Date Issued: 10-HAY-91
P(lrameter W'SIlOI-Ol 11/20/90 UK-SUOI-91 11/20/90 UK'SUfB01-01 11/20/90 UK-SUJB01-01 11/20/90
..'-. .. . .. - - - - . . - . . . . .. . . - - . ... .....-.......... --...-- --.....-... ...... --...-----...--...----............. .... .-.-..-...... ---""'''''''''..'''''''''''' ------------------------
Chloromethane (IIC/l) 10. III 10. III 10. III 10. III
Bromomethane (IIC/l) 10. III 10. U/ 10. III 10. III
Vinyl chloride (IIC/l) 10. III 10. U/ 10. UI 10. III
Chloroethane (UG/l) 10. III 10. III 10. III 10. III
Methylene chloride (IIG/I.) 5. III 5. U/ 9. II/ 9. III
Acetone (IIC/L) 10. II/IIJ 10. U/IIJ 11. B/IIJ 10. IIIIIJ
Carbon disulfide (IIG/l) 5. III 5. UI 5. UI 5. UI
1,1-0lchloroethene (IIC/L) 5. UI 5. U/ 5. UI 5. . UI
1,l'Olchloroethane (IIC/l) 5. II/ 5. UI 5. III 5. III
1,2-0lchloroethene (total) (UC/l) 5. III 5. U/ 5. III 5. UI
Chloroform (IIC/l) 5. III 5. UI 2. JI 1. JI
1,2'Olchloroethane (IIC/l) 5. U/ 5. U/ 5. ill 5. UI
2-Butanone (IIC/L) 10. III 10. U/ 10. III 10. III
1,I,I-Trichloroethane (UC/L) 5. III 5. II/ 5. UI 5. III
Carbon tetrachloride (IIC/l) 5. III 5. UI 5. III 5. III
Vinyl acetate (UG/l) 10. UI 10. U/ 10. III 10. III
Bromodichloromethane (IIC/l) 5. III 5. III 5. III 5. III
1,2'Dlchloropropane (IIC/l) 5. II/ 5. U/ 5. ur 5. UI
cls'I,]'Olchloropropene (IIG/l) 5. III 5. U/ 5. II/ 5. UI
Trichloroethene (IIG/l) 5. II/ 5. U/ 5. II/ 5. UI
Olbromochloromethane (IIG/l) 5. III 5. II/ 5. III 5. III
1,I,2-Trlchloroethane (UC/L) 5. II/ 5. U/ 5. UI 5. III
Benzene (IIC/l) 5. III 5. U/ 5. UI 5. II/
trans'I,]-Oichloropropene (IIG/L) 5. ii/ 5. II/ 5. III 5. III
Bromoform (IIC/L) 5. III 5. U/ 5. ii/ 5. III
4'Hethyl-2'pentanone (IIC/l) 10. U/ 10. U/ 10. III H). III
2'Hellanone (UG/l) 10. U/ 10. U/ 10. II/ 10. II/
Tetrachloroethene (IIG/l) 5. III 5. U/ 5. U/ 5. II/
1,I,2,2'Tetrachloroethane (IIG/l) 5. III 5. II/ 5. II/ 5. III
Toluene (IIG/l) 5. II/ 5. II/ 5. U/ 5. II/
Chlorobenzene (IIG/l) 5. III 5. II/ 5. III 5. II/
Ethylbenzene (UC/l) 5. III 5. III 5. UI 5. III
Styrene (UC/L) 5. III 5. III 5. UI 5. III
Xylenes (total) (IIC/L) 5. II/ 5. III 5. III 5. III
Note: (1) Results are reported wilh qualifiers (l.ahoratory Qualifier/Data Validation Qualifier) to the right of the vallie.
-------
TEST PITS
~
-------
. , t c:
.
ANALYTICAL OATA REPORT
Uoodstock lendflll RIIFS
Uoodstock. illinois
Metrlx: SU Type: vat
Genereted by: CAU
Dete Issued: 10-HAY-91
PerMitter W-SU(n-OI 11120/90 UK -5UOI-91 11120/90 UK-SUfDOI-01 11/20/90 UK-SUTDOI-01 11/20/90
.-............................ .......................- ......_a_.........-...-- .---.._w_-..--..-------- -- -.. -- - --..... -- - - -.. -...- - -..
Chtoromethnne (IIG/l) '0. III 10. U/ 10. III 10- III
Bromomethene (IIG/l) '0. III 10. III 10. III 10. III
Vlnyt chloride (IIG/l) 'O. III 10. III 10. III 10. III
Chtoroethene (IIG/l) 10. UI 10. III 10. UI 10. III
Methylene chloride (IIG/l) 5. III 5. III 9. III 9. 11/
Acetone (U6/l) 10. U/IIJ 10. U/IIJ 11. B/UJ 10. U/UJ
Cerbon disulfide (IIC/l) 5. III 5. III 5. UI 5. UI
1,1-Dlchtoroethene (IIC/l) 5. III 5. UI 5. UI 5. UI
1,1-olchloroethene (UC/l) 5. UI 5. III 5. UI 5. UI
1,2-Dlchloroethene (totel) (UC/l) 5. U/. 5. III 5. UI 5. UI
Chloroform (IIC/l) 5. III 5. III 2. JI 1. JI
1,2'0lchtoroethene (IIC/l) 5. UI 5. III 5. UI 5. UI
2'Butenone (IIC/l) 10. UI 10. III 10. UI 10. UI
1,I,I-Trlchloroethene (UC/l) 5. UI 5. UI 5. UI 5. tli
Carbon tetrechlorlde (UG/l) 5. III 5. III 5. IJI 5. III
Vinyl acetate (UG/l) 10. UI 10. III 10. III 10. UI
Bromodlchloromethene (IIG/l) 5. tll 5. tll 5. IJI 5. UI
1,2-Dlchloropropane (UG/l) 5. tll 5. UI 5. UI 5. III
cl.-I,3-Dlchloropropene (UG/l) 5. III 5. UI 5. III 5. UI
Trlchloroethene (IIC/l) 5. III 5. UI 5. III 5. III
Dlbromochloromethene (UG/l) 5. III 5. UI 5. III 5. UI
1,I,2-Trlchloroethane (UC/l) 5. UI 5. UI 5. UI 5. III
Benzene (UG/l) 5. UI 5. UI 5. III 5. UI
trlns-1,3-0Ichloropropene (UG/L) 5. III 5. III 5. UI 5. III
Bromoform (IIC/l) 5. III 5. UI 5. UI 5. tli
4-Hethyl-2-pentanone (UG/l) 10. UI 10. tll 10. UI 10. III
2-Hexlnone (1I6/l) 10. IJI 10. UI 10. UI 10. tli
Tetrechloroethene (IIC/L) 5. UI 5. UI 5. UI 5. UI
1,I,l,l-Tetrlchloroethane (UC/L) 5. III 5. ul 5. IJI 5. III
Toluene (UG/L) 5. III 5. UI 5. UI 5. UI
Chlorobenzene (IIC/L) 5. UI 5. III 5. UI 5. III
Ethylbenzene (IIC/L) 5. IJI 5. III 5. UI 5. UI
Styrene (UG/l) 5. III 5. UI 5. UI 5. UI
Xylenes (totel) (UC/l) 5. III 5. III 5. UI 5. UI
Note: (1) ResIII ts nre reported \Ii t/o <1"nl i fiers (I nhl\rstory 011011 fler/OstB Valldat ion ol/al I fler) to the right of the vnllle.
-------
Matrix: TP Type: VOC
Generated by: CAU
Date Issued: 02-0CT-91
"
Parameter
-.-.----------....------------
Chloromethnne (IIG/KG)
Bromomethnne (UG/KG)
Vinyl chloride (UG/KG)
Chi oroethane (IIG/KG)
Methylene chi orlde (UG/KG)
Acetone (IIG/KG)
Cerbon dlsul fide (IIG/KG)
'."Olchloroethene (IIG/KG)
'.'-Olchloroethane (UG/KG)
',Z-Olchloroethene (totnl) (UG/KG)
Chloroform (UG/KG)
'.Z-Olchloroe!hane (UG/KG)
Z-Out8none (UG/KG)
" " '-Trlchloroethllne (IIG/KG)
Carbon tetrllchlorlde (1I1i/KG)
Vinyl acetate (UG/KG)
Bromodl chi oromethnne (IIG/KIi)
1.2-0Ichloropropnne (IIG/KG)
cls-1,3-0Ichloropropene (UG/KG)
Trlchloroethene (Wi/KG)
Olbromochloromethnne (1I1i/KG)
1.',Z-Trlchloroethane (UG/KG)
Benzene (UG/KIi)
trens-' I ]-0 ichl oropropene (UIi/KIi)
Bromoform (UG/KG)
"Hethyl-2-pentonone (UIi/KIi)
2.lIeJlonone (Uli/KG)
Tetrachloroethene (1I1i/KIi)
'.1,2,2-Telnchloroethnne (lUi/KIi)
Toluene (1I1i/KG)
Chlorohenrenc (Uli/KG)
Ethyl bentCne (\Iii/KG)
Styrene (IIG/Kr.)
Xylenes (lotnl) (IIr./I:r.)
UK-TPO]-06 07/2'/91
...-..-----------------.
1600000. U/
'400000. UI
1600000. UI
1600000. UI
700000. III
17000000. O/J
780000. III
700000. III
700000. UI
700000. U/
780000. III
100000. UI
1600000. UI
780000. UI
700000. III
1600000. UI
100000. UI
700000. III
100000. UI
760000. UI
700000. III
700000. UI
700000. III
700000. III
700000. III
]000000. D/J
1MOOOO. III
700000. III
1600000. III
22000000 . 0 I J
700000. III
700000. III
700000. III
:5 10000. 0.1/.1
AIIALYTICAL DATA REPOAT
Uoodstock Lnndflll Rl/fS
Uoodstock, Illinois
UK-TPO]-06DUP 07/2'/91
------------------------
1600000. II/
1600000. III
1600000. U/
1600000. U/
780000. U/
73000000. E/J
780000. II/
780000. lI/
700000. lI/
700000. U/
780000. UI
180000. II/
1600000. U/
780000. III
780000. II/
1600000. II/
780000. II/
780000. II/
180000. U/
780000. II/
780000. III
180000. U/
700000. II/
780000. II/
780000. lI/
15000000. /J
1600000. U/
780000. II/
'600000. U/
01000000. E/J
700000. II/
J/,OOOO. J/J
100000. III
1/.00000. /J
lIote: (I) Rcr,lIlI~ MI' I"l'porl('lI \lilh fJlI.llifiers (I.lhoriltory OIl.lllfier/Ontil V.llid.ltioll Oualifier) 10 Ihe rl!,hl 01 Ilw v.llllC.
.. ,
-------
. , " ,
r ( 1.
Hatrlx: TP Type: SVOC
Generated by: CAU
Date Issued: 02-0CI.91
Parameter
............. ...... .....-..... ...... -... -.-
Phenol (UG/KG)
bls(2-Chloroelhyl) ether (UG/r.G)
2 -Ch I orophenol (UG/KG)
'.]-Dlchlorohenzene (Uri/KIi)
1.~-DlchlornhenHne (UIi/KIi)
hnlyl alcohol (Uli/KG)
'.2-Dlchlorohenzcne (UG/KG)
2-Hethylphenol (UG/KG)
bls(2~ChlorolsoproPvl )ether (IIG/KG)
'-Hethyl phenol (UG/KG)
U-Ultroso.dl-n-dlpropylnmlnc (UG/KG)
IIell8chlorOelhnne (UIi/KIi)
Ultrobcnrene (UG/KG)
Isophorone (UG/KG)
2-Ultrophenol (UG/KIi)
2.'-Dlmethylphenol (UG/k'G)
hnrolc acid (UG/KG)
his (Z-Chl oroethoxy)mel hnnc (Wi/KG)
2.'-Dlchlorophenol (Ue/KG)
1.2.'-Trlchlorohenzenc (Ue/KG)
Nephthelene (Ue/KG)
'-Chioroaniline (UG/KG)
IIexachlorohutndicne (UG/KIi)
'-Chloro-3-mclhylphenol (IIG/KG)
2-Hethylnnphlhnlenc (UG/KG)
lIell8chlorocyclopentncliene (Uli/KG)
2.'.6-Trlchlorophenol (UG/KG)
2.'.5-Trlchlorophenol (LJIi/KIi)
Z-Chloronnphthalenc (Wi/KG)
2-Ultroanlllne (UG/KIi)
Dlmcthylphthnlnle (Uli/KG)
Acennphl"ylene (UG/Y-li)
2.6-0Inllrolol,"enr. (1If./I:f.)
3-111 Ironnll ine (ur./r.r.)
!tcennphl hene 11Ir./I:r,)
2.'.-Oini I'nphr.n,,1 (1If./r.f.)
~'lIitrophl'''ol IlIr,ft:f.)
IIole: (1) Re!;IIII r. ill I' r"I'0,.I(''' ui Ih
ANALYTICAL DATA REPORT
Uoodstock Landfill RI/FS
Uoodstock. 1IIInol5
UK-TP03-060UP 07/2'/91
UK-TPOJ.Oh 07/2'/91
--... ..---........ --........ ------........
......-.....",.......... --... -.............
100000.
100000.
100000.
100000.
100000.
21000.
12000-
100000.
100000.
100000.
100000.
100000.
100000.
6000000.
100000.
100000.
500000.
100000.
100000.
100000.
100000.
100000.
100000.
100000.
100000.
100000.
100000.
500000.
100000.
500000.
100000.
100000.
100000 .
500000.
1000011.
')1I0110n.
0;000011.
'1",11 i Ii..,.,;
U/UJ 300000. U/UJ
U/IIJ ]00000. LJ/UJ
IJ/IJJ 300000 - U/UJ
IJ/UJ ]00000 - U/UJ
U/IIJ 300000. U/UJ
J/J 300000. U/UJ
J/J 300000. U/UJ
U/IIJ 300000. U/UJ
IJ/IU 300000. U/UJ
II/IJJ 300000. U/UJ
IJ/UJ 300000. U/UJ
U/IIJ 300000. U/UJ
U/IJJ 300000 - II/UJ
£/J '600000. /J
U/IIJ 300000. U/IJJ
U/IIJ 300000. U/UJ
IJ/IU 1500000. U/UJ
u/UJ 300000. IJ/UJ
II/UJ 300000. U/IIJ
U/UJ 300000. U/tJJ
tJ/IIJ ]00000. U/tJJ
tJ/IU 300000. U/UJ
II/IJJ 300000. U/tJJ
Il/tU 300000. U/IIJ
U/UJ ]00000. II/IIJ
II/IJJ ]00000. U/UJ
tJ/UJ 300000. U/UJ
U/tJJ 1500000. II/UJ
U/IJJ ]00000. U/UJ
u/IJJ 1500000. U/UJ
IJ/IJJ )00000. U/UJ
II/IIJ 300000. U/UJ'
II/IIJ Jonnno. II/IIJ
II/IIJ 1500000. II/IIJ
11/11.1 JOOOOO. u/uJ
11/11.1 1500000. u/UJ
11/11.1 1')00000. II/UJ
II ,,!>o,.ntorv 011011 i I ier/Oaln Viii iclal ion 0110111 fier)
10 !he rillhl III Ih(' v"III~.
-------
ANAlYJICAl DAJA REPORJ 2
Uoodstock lendtlll Ri/fS
Uood5tock, IIIInol5
Hetrlll: JP Jype: SVOC
Perimeter UK'TPO]-06 07/24/91 UK'TPO]'060UP 07/Z4/91
..........-----------.-------- ---.-.------------------ ---------------...-----.
olbenrotllrlln (UG/KG) 100000. II/IIJ 300000. U/UJ
Z,4-0lnltrotolllene (1I1i/Y.Ii) 100000. U/IIJ 300000. II/IIJ
olethyiphtheillte (\lG/KIi) 100000. 1I/IIJ 300000. U/UJ
"Chlorophenyl-phenylethrr (\Iii/KG) 100000. 1I/IIJ 300000. U/IIJ
rt uorene (UG/H,) 100000. li/UJ 300000. II/I/J
"Nitroeniline (\lG/Y.G) 500000. U/UJ 1500000. II/UJ
',6-0Inltro-Z'methylphenol (UG/KG) 500000. U/UJ 1500000. U/UJ
N-nltr05odlphrnyl nmine (\lG/KIi) 100000. U/IIJ ]00000. U/IIJ
,- Bromophenyl- phenyl ether ClJG/KG) 100000. U/UJ ]00000. II/IIJ
IIuechlorohenlene (tIG/KG) 100000. IJ/IIJ ]00000. U/IIJ
Pentachlorophenol (\lG/Y.G) 500000. U/\lJ 1500000. U/UJ
Phenanthrene (UG/KG) 100000. U/UJ 300000. U/UJ
Anthracene (UG/KG) 100000. II/IIJ ]00000. II/UJ
Ol'n-butylphthelnte (tlG/KG) 100000. U/IIJ 120000. J/J
fluoranthene (UG/KG) 100000. II/UJ ]00000. U/UJ
pyrene (UG/KG) 100000. U/IIJ 300000. U/IIJ
Butylbenryiphthlliote CUG/k'Ii) 100000. U/IIJ 300000. tI/IIJ
3,3'-Olchlorohr.nzldlne (UG/KG) ZOOOOO. U/UJ 600000. U/UJ
Denzo(e)anthrncene (UG/KG) 100000. U/tlJ ]00000. U/UJ
Chrysene (UG/KG) 100000. U/IIJ ]00000. U/UJ
bls(2-ethylheKyl )phthnt ote (\lG/KG) 250000. J/J 76000. J/J
ol-n-octyl Phlhnlote (\lG/KG) 100000. IJ/UJ 300000. U/UJ
Benzo(b)flllorllnthene CUG/KG) 100000. II/IIJ ]00000. II/I/J
Benzo(k)fluorllnthenc (IIG/Y.(i) 100000. U/IIJ ]00000. tI/UJ
Benlo(e)pyrenc (IlG/KG) 100000. II/IIJ ]00000. II/I/J
Indeno(1,Z,]'cd)pyrcne (IIG/KIi) 100000. II/IIJ ]00000. U/I/J
Dlbenz(e,h)enthrncenc (UG/KG) 100000. II/II:' 300000. U/IIJ
Benzo(g,h,l)pcrylcne (UG/KG) 100000. II/IIJ 300000. II/UJ
lIotr.: (1) II..~;"II" iI'" ""I",,-,,'rI "ith ",,;lIili,',,; Il;lhnr;tlory Ollalilil'r/Ontn Validation OIl.~litier) In the ri!.hl III Ih" v"I\II~.
, :
" .
-------
. t
(, :
r..
1:--
ANALYTICAL DATA REPORT
Voodstock Landlill RI/IS
Uoodstock, Illinois
Hlltr!!.: TP Type: ppeo
Generated by: CAU
Date Issued: 02-0(T.91
Parameter; vr-TPOJ-06 07/2~/91 VK-TPO]-060UP 07/24/91
-.-.- ...................... .............. .... .............. .......--........ ....-................----
IIlpha'OIlC (Wi/K(j) 12. II/UJ 10. II/UJ
beta-OIlC (HG/KG) 12. II/UJ 10. U/UJ
delta-OIlC (H(j/KG) 12. U/UJ 10. U/IIJ
gll/ffM' OIlC (Li nc1nne) (HG/KG) 12. II/UJ 10. U/UJ
lIeptachlor (HG/KG) 12. II/UJ 10. U/IIJ
Aldrin (H(j/KG) 12. U/IIJ 10. II/IIJ
lIeptachlor epoxlde (HIi/KIi) 12. U/IIJ 10. II/UJ
Endosulllln I (tIG/KG) 12. 1I/IIJ 10. II/IIJ
Dieldrin (HG/KG) 2~. U/UJ 20. II/IIJ
~,~'-ODE (H(j/KG) 2/,. U/IIJ 20. U/IIJ
Endrln (HG/KG) 2~. II/IIJ 20. II/IJJ
Endosul , an II (HG/r.G) 21,. IJ/IJJ 20. II/IIJ
~,~'-OOO (H(j/KG) 2~. U/IIJ 20. U/IIJ
Endoslll Ian 5111 101 e HIli/KG) 2~. II/IIJ 20. U/IIJ
~,~'-OOT (HG/KG) 2~. U/IIJ 20. U/IIJ
Hethoxychl or (H(j/K(j) 160. II/UJ no. U/IIJ
Endrln ketone (H(j/KG) 2~. II/UJ 20. U/UJ
alphll-Chlordnne (tIG/r.r.) 120. II/IJJ 100. IJ/IJJ
gaRmIl-Chlordane HIli/KG) 120. II/IIJ 100. U/IIJ
Toxaphene (HG/KG) 21,0. U/IIJ 200. U/UJ
Aroclor-1016 (Hli/KG) 120. II/UJ 100. U/IIJ
Aroclor-1221 (Hli/KG) 120. II/IIJ 100. U/IIJ
Aroclor-12]2 (HG/KG) 170- U/IIJ 100. U/UJ
Aroclor-121.2 (Hr./y'(j) 120. II/IIJ 100. U/UJ
Aroclor-12~0 (H(j/y'(j) 120. II/IIJ 100. II/UJ
Aroclor-1254 (H(j/I((j) 1/,0000. I:/J 120000. C/J
Aroclor-1260 (H(j/Y.G) 2~0. II/IJJ 200. II/UJ
" ,
IIole: (1) "''',11'1,; ;,1"" 1""'"'1"1.''' "ilh 'I""Ii/i,',,; (I:,hnl'illo,.y O"illifi'~"/I1i1I;1 v;,li,I"llon f)lIilli'i"r) 10 Ihe ,-i!!hl III Ih" v.)I,",.
-------
A"ALYTICAL DATA REPORT
Uoodstock tnnd'lll RI/fS
Uoodstock, Illinois
Hlltrlx: TI' Type: SLI"O Hfl
Generated by: CAU
Date Issued: 02.0CI-91
I'nrllmelc:r UK'TP03-06 07/2(/91 Uk:-TP03.06nIJP 07/2(/91
-.-........-............ .... .........",...... ........................-..-... ....a___.._---.-..-------
Alumlnll1l (HIi/k:Ii) 31.] tJ/ ]1.2 U/
Antlmonv (HG/KIi) 31.3 U/ 31.2 U/
Arsenic (Hli/KG) 1.3 II/ 1.2 II/
hrhl1l (HG/k:Ii) 6.3 U/ 6.2 U/
Bervl! hili (HIi/KIi) ].1 tJ/ ].1 UI
Cllchlt", (Hli/KG) ].1 tJ/ ].1 U/
Caldun (Hli/KG) 626. II/ 624. III
ChrOlllhl1l, tolnl (HG/KIi) 6.] 11/ 6.2 UI
Cobalt (HG/KIi) 6.] II/ 6.2 UI
Copper (HIi/KIi) /.1 tJl 6.2 UI
Iron (HG/KIi) ~II, K/ 29.3 K/
lend (Hli/KG) 1.9 tll 1.9 U/
Hagneslum (Hli/KG) 626. U/ 624. U/
Hllngllnese (HG/KG) 6.3 III 6.2 UI
Hercury (HG/KG) 0.15 *1 0.12 11*1
Nickel (HG/KG) 12.5 III 12.5 U/
Potesshl1l Hili/KG) 62.6 II/ 62.4 UI
Selenlull (Hli/KG) 1.3 UI 1.2 II/
5 II ver (Hli/KIi) 6.3 III 6.2 u/
Sodium (HG/KG) 1250. U/ 1250. U/
Thllil ill1l (HG/KG) 1.9 tI/ 1.9 UI
Vanadium (Hli/KG) ]1.] tll 31.2 UI
ZInc (HIi/KIi) 6.3 UI 6.2 UI
Cvanlde (HG/KG) 7.9 U/ 7.8 III
Total Solids (X) ]1.7 / ]2. I
IIn'," fI' fI,","II': ;,,-,. """orl"" lIi.h '!1I;lIi/i,-,-.; (I "hor.'lory Olli'llili"r/Oi'lln V.,li.Ii'lllon Oll;'llificr) 10 Ihe dnlll of Ihl' viltl/I'.
, ,
" ,
-------
SI.:~~1~! OF i:.i~i:V:~Y !~:~iiF!:O C~~~~:S
~ocCs:oc~ Lanefill ~!/FS
~ocCs:ocic. ! II il"lQis
~a:~iJ:: i;>
C~~e~a:~ ~: C~~
:a~e !ss:..:e-:: C2.C~i.;'
1.'(-i;:03,06
Ci 12'/91
(i;~~) ie~:a:;vely-icen:;fi~ Semi-Volatiles
:~Ur'C (Un;:5)
.------...--..---......-...------------.-.-
3-Cyctonexene-1-methanol,
~:3 (UG/X:;)
pes '~G/J::;)
?:s (UG/J::;)
pC; (u::/I::;)
pe; (UG/J::;)
PC; (UG/X::;)
pc; (u:;/XG)
PC; (UC/I::;)
?ca (I.::;/X::)
pca (UC/I:::;)
PCS (UG/XG}
PC; (UC/J:Ci)
PCS (UCi/J:Ci)
Hetnylpnenylester
Unknown (UCi/(Ci)
Unk:"\own (UG/II:Ci)
Unknown (UG/(Ci)
Unknown (UCi/II:Ci)
Unicnown (UC/J::C)
.alp (UG/XG)
(UG/II::;)
-
Concentl"at;O<'\
LC/""'::
.----..--.-........--.----......
1600000. J/ ~~
5000000- ~/J~
1aooooo. ~/.Hl
2900000. J/~N
'100000. J/JII
7200000. J/~'S
1'00000. J/ JH
3500COO. J/JII
,(.oecoo. J/JII
1600000. J/J~
5100000. J/JII
1900000. J/JH
2/'00000. J/ JH
3700000. J/JW
1700000. J/J~
2/'00000. J/JW
2900000. J/JII
3:'00000. J/JII
3100000. J/JII
2300000. J/JII
-------
SU~MA~T OF TENTAiIVE~T IOEUTIFIEO C~~OU~:S
~ooCs~ock landfill ~I/FS
~ooCstock. Illinois
Matrix: T~
~I:' i;>03. 06.:!U?
07 /2~/91
(ioWA) Tentatively-Identified Semi-Volatiles
C~ (Units)
COt1Centra~ion
..............-.........-.......
lQ/OVO
--....-.-........-............-------......
PCS (Ue/J::e)
PCS (Ue/J::e)
PCS (Uc/J::e)
PCS (Ue/J::..)
PCS (ue/J::e)
pes (ue/J::e)
pea (ue/J::e)
pca (u../J::..)
PCS (ue/J::..)
PCS (Uc/r:C)
PCS cue/r:..)
pca (UC/J::C)
pcs (ue/J::C)
PCS cuc/J::e)
Tris(methylphenyl)esterphospho
Unknown (Ue/KG)
Unknown (UG/KG)
Unknown CUG/ICG)
Unknown (UC/KG)
Unknown (UG/KG)
(UG/ICG)
3000000.
960000.
15COOOO.
3000000.
8100000.
2000000.
1'.00000.
3600000.
5100000.
1200000.
5700000.
1800000.
2500000.
3600000.
1300000.
1900000.
2300000.
2900000.
1700000.
1000000.
2
J/JN
J/JW
J/JW
J/JW
J/JU
JlJW
J/JW
J/JW
J/JI/
JlJI/
JlJI/
J/JI/
J/JI/
J/JI/
J/JW
JlJI/
J/JW
J/JI/
JlJW
J/JI/
-------
'",
SURFACE SOIL
..
".
-------
. \
I" :
r- r.
.. ~:~.:.:.j.... ,".
"
,.. .
'.
'~
I. .
- ,
ANALYTICAL DATA REPORT
Uoodstock land' III RI/FS
Uoodstock. 1IIInol5
Hatrllc: 5S Type: SlIIID HTl
Generated by: CAU
Date Issued: 01.0CT.91
Parameter UK-SSOI'O\ 08/08/91 UK'5S02-01 08/08/91 UK-SS02-9\ 08/08/9\ uK-SSOJ-OI 08/00/91 UK'SSO~-O\ 08/08/91
..............--................-.......... --..- ............... .---....... ..... -... ....---.................- ............ .... .. .... .... ...... .. .... .... .. .... -...--- .-- -----...... -... .-.. -...-..-----------"--"-.
Ahmlnlm (HG/KG) 10500. I 4J20. I n~o. I 17000. I 6610. I
Antimony (HG/KG) 12. 1111 III J 11.4 tJII/IIJ 11.5 UII/UJ 10.8 IIII/IJJ 8.8 IJII/IIJ
Arsenic (HG/KG) J.9 51 4.6 51 J.6 51 5.1 51 ].J 51
88r1un (HG/KG) 209. I 45.6 1:1 40.4 KI ~\2. I 610.~ I
Oerylilim (HG/KG) 1.2 III 1.1 III 1.1 III 1.1 III 0.60 III
Cactnhm (HG/I:G) I.J I 1.1 III 1.1 III 2.3 I 0.80 III
Calchlll (HG/KG) 5\900. / 66100. / ]9000. I 41600. I 51000. I
Chromlull. totnl (tIG/KG) 75.1 / 5.6 / 1. / 63.1 I 9.6 I
cobalt (HG/KG) J.4 '#:1 2.9 1:1 J.4 KI 6.4 KI ~.1 1:1
Copper (He/KG) 283. / 11.1 / 16.1 I 509. I 10.2 I
Iron (HG/KG) 101.00. I 12100. I 11100. I 2~/.00. I 12200. /
Leod (HG/KG) 1,1..9 "/J 28.2 .0 \9.9 "/J H.6 S"/J 17.4 "/J
Ha!Jnes hili (HG/KG) 21,900. / 34000. / 10000. I 10900. I 30300. I
Hanganese (HG/KG) 395. / 1,1,5. / 280. / 793. I 441. I
Hercury (HG/KG) 2.2 ./J 0.12 ./J 0.09 ./J 1.9 "/J 0.01 "0
Nlcket (HG/KG) 21.1 / 13. / 11.6 I 51.5 I 16.8 /
potasslllll (He/KG) 1020. KI 651,. 1:/ 123. 1:/ 1770. I 001. I
5elenhm (HG/r.G) 0.9J KSI 0.49 IISI 0.92 KSI 1.9 SI 0.41 IISI
5 II ver (HelKe) 6.1 / 2.J III 2.3 III \0.] I 1.0 III
Sodlun (HelKe) 1,61. III 451. III 459. III 1000. K/ ]52. III
That Ilun (HG/KG) 0.6/. III o.n III 0.51 III 0.61 III 0.61 III
Vonadhm (tIG/KG) \2. III 11.~ III 11.5 II/ 10.0 UI 15.5 I
Zinc (HG/KG) 1.1.1. I 59.1 / 61. / 600. I 5/..6 I
Total Solids 00 n.1 / 71.0 / 15.2 I 16.4 I 02.1 I
IIn.,,; (1) 11''';1111'; ,.1'1' ,,'po...,.,1 ..ilh "",,,"i,',.!; (I "llfu'o1Iory n"al ilicr/I1;,liI villi,'alion Ollali(i"n
In "U~ ,-j!,h. "' ,I..~ VI.tllt~.
-------
ANALYTICAL OATA REPORT
Uoodstoek Lend' III RI/fS
Uoodstoek, ""nol5
HetrlK: SS Type: SVOC
Genereted by: CAU
Oete Issued: 01.0CT.91
rernmeter ur.SSOI-01 00/00/91 UK-SS02-01 08/08/91 UK-SS02-91 00/00/91 UK-SSOJ-01 00/00/91 UK-SSO~-OI 08/00/91
.-...-...-...-----.. ---- - --.... ------ -- ..........---.........-..-. -----..-..-.-...-...--------..- ------..........-........ -....... -... --... -.. ....-..... --.. --...... --...- ..... .... .. .. .. .. ... .. .. ............. .. .. .... .
Phenol (UG/KG) '50. III 390. III '50. II/ ~50. III ~20. III
bls(2-Chloroethyl) ether (IIG/KG) '50. \J! 390. II/ '50. III '50. III ~20. III
2-Chlorophenol (IIG/Kr.) 1,50. III 390. III '50. II/ '50. III ~20. III
1,3-Dlchlorobenzene (lIli/Kr.) 1,50. II/ 390. UI '50. II/ '50. II/ '20. III
1,~-Dlehlorohenrene (IIG/Kr.) 1,50. II/ 390. III '50. III '50. III ~20. III
Benryl eleohol (UIi/KIi) 1,50. III 390. III '50. III ~50. III ~20. III
1,2-0Iehlnrobenzene (lIli/KIi) 1,50. III 390. II/ '50. III '50. III ~20. III
2'Hethylphenol (IIG/Y.Ii) (,50. II/ 390. III '50. III ~50. II/ ~20. III
bls(2-Chloroisopropyl)ether (IIG/KG) 1,50. II/ ]90. III '50. III '50. III ~20. II/
'-Hethylphenol (IIG/Y.G) ~50. II/ 390. U/ '50. UI ~50. III 420. III
N-N I troso-dl'n-dipropyl mnin/! (lJ(i/KG) 1,50. III 390. II/ '50. II/ '50. III 420. II/
HeMachloroethnne ("G/KG) '50. III 390. U/ '50. II/ ~50. II/ 420. III
Nltrobenrene (UG/Y.G) '50. II/ 390. U/ '50. III '50. 11/ '20. II/
Isophorone (IIG/KG) 450. II/ 390. II/ '50. III '50. II/ 420. III
2-111 trophenol (IIG/KG) '50. II/ 390. II/ '50. III 450. U/ '20. III
2,"Olmethylphenol (UG/KG) (,50. II/ ]90. II/ '50. II/ '50. U/ UO. III
Be",ole: lIeld (IIG/KG) noo. III 1900. II/ 2200. U/ 2200. U/ 2000. II/
bls(2'ChloroethoKy)melhnne (1I1i/Y.Ii) 450. III 390. U/ '50. III '50. U/ '20. II/
2,"Olehlorophenol (IIG/KCi) 1,50. II/ ]90. U/ 450. II/ 450. III '20. III
1,2,'-Trlchlorohenzene (IIG/KG) 1,50. III ]90. II/ '50. II/ 450. '" '20. III
"aphtholene (IIG/KIi) 1.50. II/ ]90. III '50. II/ 450. U/ (,20. II/
'-Chlorooniline (IIG/KG) 200. JI 390. II/ '50. III go. JI ~20. III
lIeKnchl orohut ndl ene (IJIi/I:G) 1,50. III ]90. U/ (,50. III (,50. III 420. III
"Chloro.J-methylphenol (lIli/r.li) 1,50. III ]90. II/ '50. III (,50- III UO. II/
2-Hethylnllphlhnlcne (III;IYG) 1,50. III ]90. III (,50. III (,50. III UO. III
lIuoehl oroeycl opcnl ncl i ene (1I1i/r.1i) (,50. III ]90. III '50. III '50. III '.20, III
2, I, ,6- T rich I orophenol (1Ir.1Y.1i) 1,50, III ]90. UI (,50. III 1.50. III UO. III
2,I,,5-Trlchlorophenol (1I1i/t:1i) 27.00, III 1900. III 2200. III 2200. III 2000. III
2-Chloronnphthnlen!! (IIG/Y.r.) 1,50. III J90. III (,50. III ~50. III 1,70. III
2-lIllronnil ine (lIli/r.li) noo. III 1900. III noo. III 7100, III 7000, III
Dimethyll'hthnlnle (Illi/rr.) I,~n. III J90. III 1,50. III lOll, JI I,ln. III
Acennphlhylene (1Ir./r.r.) '.!io. III J?O. III 1,50. III 1,50. III '.In. II/
2,6-0inilrolo'"enr. (IIIi/l:q I,~.n. III J?O. III 1.50. III 1,50. III 1,711. III
J-lIitrnnnil i,l(' (lIIi/l:r.) 771111. III I?OO. III nno. III noo. III 7(1111). III
/I('nllphlh('/I(' (IIr./n;) ',',0. III J?O. III I,~O. III I.~)O. III 1,7/1. III
2,1"1\ i ni I rnplH'noi (111;/1:1;) ;I;tno. III I?OO. III 2700. III noo. III ;'111111. III
~'lIitroph('n()1 (111;/1"/;) ;';>1111. III I?OO. III non. III 7711/1. III 711/111. II/
1!:"It.!: (I) II"
-------
, , , , ',
I
AIiAlYTICAl DATA REPORT 2
Uoodstock landliit RI/FS
Uoodstock, illinois
Hotrlx: SS Type: SVOC
Parnmeter UK'SsOI-OI 08/08/91 UK-SS02-01 08/08/91 UK-SS02-91 08/00/91 UK-SS03-01 08/00/91 UK-sSO~'OI 08/08/91
...___e- ............................ ~.............. .. ..........-....,,"" ........----- ..-- ..- ---....- ---.... ----.....-...... ............... .. .. ........... .... .. ... ... ..... .. ..... ....... .."''''' ---- -........ ..--_...... -.. ......-....-.--......................
ofbcnrofurnn (1Ir./Kr.) ~50. III 390. III ~50. III ~50- III ~20. III
2,~'Olnltrotoluene (1Ir./KIi) ~50. III 390. III ~50. III ~50. III '20. III
Olethyiphthaillte (IIG/KG) 450. III 390. III ~50. III ~50. III ~20. III
~-Chlorophenyl-phenylether ("G/KG) ~50. III 390. III ~50. III ~50. III '20. III
Fluorene (IIG/Kr.) ~50. III 390. III ~50. III 450. III '20. III
~-"ltrOllnfllne (IIG/KG) 2200. III 1900. III 2200. III 2200. III 2000. III
~,6'O Inl tro. 2.melhyl phenol ("li/KG) 2200. III 1900. III 2200. III 2200. III 2000. III
N'nltr05o<1ip/lI~nyl nmlne (IIG/KIi) ~50. III 390. III ~50. III 450. III ~20. III
~'Dromorhenyl'p/lenyl elher (IIG/KIi) 450. III 390. III 450. III 450. III 420. III
lIeKach I orohen! ene CUli/KIi) 450. IJI 390. III ~50. '" 450. III 420. III
Pentachlorop/tenol (lJG/KG) 2200. III 1900. III 2200. '" 2200. III 2000. III
Phenanthrene (lili/KG) 50. JI 390. III 450. III 79. JI UO. III
Anthrncene (IIG/Kr.) 1.50. III 390. III ~50. III 450. III UO. III
DI-n-hutylp/lthnl nle (IIG/KIi> 210. JI 61. JI 99. JI 240. JI 90. JI
fluornnthene (IIG/KIi) BO. JI O. J/ 59. JI 220. JI 61. JI
pyrene (IIG/KIi) 91.. JI 52. JI 63. JI 760. JI 420. III
Dutylbenlyiphthnillte (lIli/KIi> 65. JI 390. III 450. III 290. JI 420. III
3,3"Dlchlorohenlidlne (lIli/KIi) 900. III 780. III 890. III 900. III MO. III
Benlo(a)nnthrncene (IIG/KIi) n. JI 390. III ~50. UI 160. JI 420. III
Chrysene (lili/KG) 93. JI 390. III ~50. III 180. JI 420. III
bls(2.ethylhexyl )phthnlnte (lili/KIi) 1.50. '" 390. IJI ~50. III 1800. DIll 420. III
DI-n-octyl Phlhnlnte (IIG/Kr.) 1.50. III 390. III ~50. III ~50. III 420. III
Denlo(!» fluoronthene (IIG/r.Ii) 300. JXI 390. III 450. III 690. XI 420. III
Denlo( k)t I IIornnl hene (lIli/Kr.) 300. JXI 390. III 450. III 690. XI 470. III
Denlo(a)pyrene (Uli/r.li) 99. JI 40. JI 450. III 170. JI 470. III
I Meno( 1,2,3 - CII)pyrene (lIli/KIi) 1.50. III 390. III 450. III 100. JI 4}0. III
Dlhenr(n,h)nnlhrncene (IIG/r.Ii) 450. III J90. III ~50. III 48. JI 420- III
Benro(!!,h, i )perylene (Illi/r.r.) 52. .11 390. III 450. III 110. JI 420. III
lIote: (1) nr=~.lItt.; il'" If'pn''I~'d \Iii" (11I.dili,o", (lilhu,.iltUI'Y nUidificr/Oatn V.,licl;,.ion ouatificr) to the l'i~lh' fit the v;,hll:.
-------
S~~~~T OF iE~iAiIV:~T IOESiIFI:~ C~FOUHCS
~coCs~;ck landfill ~I/FS
\Jooc:s~oc:it. III inc i S
j:~ix: 5S
~!"Iera:e<: by: C..1:J
3:1: ISSI.:e<:: OJ -CCi-91
('S501.01
08/08/91
(T;NA) Tentatively' Identified 5~i-Vola~iles
C~ynd (Units)
..........-.-------------.----------.-.-.-.
Unknown (UG/ICC)
Hexadecanoic acid (Ue/ICe)
Unknown amine (UG/ICG)
Unkno.n CUC'ICe)
Unknown CUC'ICC)
Unknown Sl.:cst. hydrcc:ar:cn (UG/IC~)
Unicno.n CUCi/IC:;)
Unknown (UG/IC:;)
Unknown hydrocarbon (UG/ICC)
Unicnown CUCi/ICC)
Unknown (UCi/ICC)
Unknown hydrocarbon (UG'ICe)
Unknown oxysenated hydrocarbon (UG'ICe)
Unknown (Ue/ICC)
Unkno.n CUG/ICC)
Unknown (UG/ICC)
Unknown CUG/ICC)
Unknown cue/tC)
Unknown CUG/tC)
Unicnow-n (Ue/tC)
Cor.ce!"lt ra t i 0"
~C/OVQ
-.--------------.-------------..
60:.0.
730.
1800.
5'7!J.
530.
1300.
730.
820.
2eCO.
82C.
820.
1300.
1800.
1000.
7aO.
1300.
2200.
1200.
2,00.
530.
JI//N~
J/NJ
J/NJ
J/NJ
JIHJ
J/HJ
J/I/J
J/NJ
J/I/J
J/I/J
J/IIJ
J/IIJ
J/IIJ
J/IIJ
J/IIJ
J/NJ
J/NJ
J/IIJ
J/I/J
J/NJ
-------
.~at:-ix: 55
/('SS02.01
S~~~~~T OF TcNrArIV:~T ICeNTIFIE~ C~~~~CS
~ooCS:OCl Lanefill RI/FS
lOooc:s:od, Illinois
C2/C8/91
(iSNA) ien:a:i~ely-lcentifieC S~;,vota:iles
LQ/::'/C
'.1:' SS02' 9 1
Comco~TC' (~n;ts)
Concentration
....-.....------.......-.--.----.....-.----
....-----...-------....---.---..
Unknown oxygena:eC alkane (UG/X::;) 670. UNJ
Unknown oxysena:ee alkane (UG/I::;) ~ 70. J/W.J
Hexadecanoic acid (UG/X::;) 590. UNJ
Unknown hydrocarbon (UG/X::;) 590. J/U.':
Unknown hydrocarbon (UG/X::;) '30. J/NJ
Unknown s..:s:. hydrocal"bon (UG/(::;) i ;00. UNJ
Unknown hydrocarbon (UG/X::::) 3~0. ..1/)(':
Unkncwn s;.;:s:. hydr-ocal"bcn (~:;/(:;) 3eCO. J/NJ
Unknown (UG/X::;) 1500. J/N J
Unknown oxygenated hydl"ocal"bon (UC/x::;) 2500. J/NJ
Unknown oxygenated hydr-ccal"bon (UG/X:::;) 23000 . J/'t;J
Unknown oxysenateC hydl"ocal"bcn (UC/x::;) 510. J/NJ
Unknown hydrocarbon (UG/X::;) 21:;0. J/IIJ
Unknown suest. hydrocal"bcn (UG/X:::;) 2CiCO. J/NJ
Unknown CUG/J::G) no. J/NJ
Unknown (UG/X:G) ~~O. J/NJ
Unknown (UG/x:G) noo. J/NJ
Unknown hydrocarbon (UC/):::) !20. J/NJ
Unknown (UG/X:G) 670. J/NJ
Unitl'lOwn (UG/X:G) 3100. J/NJ
08/08/91
(TSNA) Tentatively'ldentified Semi-Volatiles
LQ/OVC
,-
1'..:-
~
CompoYnd (Units)
Concentration
--------------------.-..--.-.-.-...-------.
---.------....----....-------...
Unknown oxysenateC alkane CUO/X::;) 720. J/NJ
Hexadecanoic acid (UG/X:G) 5'0. J/"'2
Unknown oxysenatee hydrccarbon (UG/I::;) 1200. J/IIJ
Unitno.n s~st. hycl"ccarbcn (ue/x:;) 2!!CC. J/"J
Unitnc.n (UG/x:e) c.::~. .!/!oi':
~n~nc.n oxysenateC hyc~::a~~n ((;::;/x:::;) c ~::. ~/....~
Unknown sl.'bst. hydrccarbcn (UC/x::;) 7600. 2/\;2
Unknown (UG/ICC) 630. J/~')
Unknown (UG/XC) sec. J/S.2
Unknown hydrocarbon (Uei/X::::) ,~CO. J/NJ
Unkncwn hydrocarbon (Uei/XC) ....'" J/1I2
Ift",;'w.
Unkno.n CUG/ICG) i2C. J/);J
Unknown CUG/IC:;) 12:. J/NJ
Un~nown (UG/IC:;) 13:;0. J/);J
Un~no.n hydroca~:cn (\;::;/X::;) "CO. J/);J
Uni:no.n CUG/ICG) 9'90. J/~J
Un~nown CUG/X:;) 210. J/~J
L:nknc.n (UG/IC(j) ~5CO. ~/'N.!
L:ni:no.n (UG/XC) 5~C. J/);J
Unknown (UC/ICG) 72Q. J/SJ
-------
S~~~~~ OF TESTATIVELT ICESTIFIE~ C~p~~CS
-o6Cs~ock Lanefitl RI/FS
-
',;ooc:s~oci:, Il
.~;s
a~r;x: SS
::.SS03'01
08/08/91
(TaIlA) Tentat;vely'!den~;f;~ S~;,vola~;les
Corrcourd (Units)
C~entraticn
lC/OVQ
..-----.-.....---..........-..........-.-..
--......-.-.---.-----.--..--.-..
Hexadecanoic acid (UC/~~) 1300. J/NJ
Unknown.chlorinat~ hyerocarbo (UC/~~) 1100. JlIIJ
Unknown sUbs~ituted alkane CUC/~~) 2300. J/IlJ
Unknown CUC/IC~) 1200. J/NJ
Unknown CUC/ICG) 1200. JlIIJ
Unknown CUC/IC~) 2200. JlNJ
Unknown oxysenated hydrocarbon CUw/~G) 2700. J/IIJ
Unk:"\own (UC/IC~) 1200. J/IIJ
Unknown CUC/IC~) 1500. JlIIJ
Unknown CUC/ICC) 1600. J/IIJ
Unknown oxygenated hydrocarbon (UC/~~) 1600. JlIIJ
Unknown cue/ICG) 2100. JlIIJ
Unknown CUC/IC~) 1500. JlHJ
Unknown oXYgenat~ hydrocarbon (UC/~C;) 5000. J/HJ
Unknown cue/ICG) 1200. J/IIJ
Unknown hyerocarbon (UC/ICC) 1200. J/IIJ
Unknown cue/leG) 2600. J/NJ
Unknown CUG/IeG) 3100. JlIIJ
Unknown (UG/IeG) 260C. JlIIJ
Unknown CUG/IeG) 2800. J/'l/J
.1:-SS0l,-01
08/08/91
CTBIIA) Tentatively-Identified S~i-Volatiles
C~urd CUn its)
Concentrat; on
LC/DVC
------.-.--------------....----....--------
--.--.-----.....----------------
Unknown CUC/IeG) aoo. J/IIJ
Unknown CUC/IeG) 930. JI'l/J
Unknown cue/leG) 1200. J/IIJ
Unknown CUC/IeG) i20. J/IIJ
Unknown CU(j/'(~) no. 5J/!.'J
UnknolOn (UC/'(:) .....,.. ~/~.:
\' \01,,",-
Unknown cue/lee) naco. J/\iJ
Unknown CUG/IeG) 5;0. J,'\i~
Unknown hyerocarbcn CUG/IeG) 2100. J/.';
Unknown CUG/IeG) 1100. J/IIJ
Unknown cue/lee) 1200. J/'"
UnicnolOn CU~/ICG) 670. .;/s~
Unkr:olOn CUC/XC) ;iC. ,,/'"
Unknown CUC/Ie:;) 1500. J/,J
Unkr~IOn hydrocarbon (UC/~C) ;;0. .1./S';
UnknolOn CUC/XC) 2!.:0. J/,':
Unitrlown CU(j/ICG) SC;O. J/.J
UnknolOn CUG/X:;) 1,600. J/II"
Unknown CUC/X~) 160C. J/'"
Unknown CUC/X~) 510. J/IIJ
-------
v
..,.
AQUIFER MATRIX
.-
..
;;
-------
, ..
, i'
r.
l
Hetrlx: S8 Type: SUllO
Genereted by: CAU
Dete Issued: 10.HAY.91
P8remeter
.....................-..............
Tote! Orgenlc Cnrbon (HG/KG)
Cetlon Exchen~e Cnpnelty (HEO/l)
ANALYTICAL DATA REPORT
Uoodstoek lnndflll RIIFS
Uoodstoek, illinois
UK.SBMUOID.OO.5 07/27190 UK'SOHUOID.~1 07/30/90
-.---.......--.-----------
UK-SRHU02.'3 08/03/90
16000.
O.
....-.------------...---
>1
III
16000.
o.
16000.
3.95
..................... ..-..-....---..-.-..
UK.SOHU02.60 08/0]/90
>/
II/
>1
/
16000.
O.
...... ----............. "''''.''- -....--..-
UK.SOHUO].06 00/06/90
u....._- '1\ Onc-o.ltr ..r'" r,......,..,..t....,1 .,;... ,..1I:.lili,..,..-: Ilnhnrntnrv oUAllfirrJnnln Vnli"i\tlnn oURllller) 10 the rioht nf the value.
>/
II/
16000.
o.
........-............ ...... -. ----......
>/
lI/
-------
Matrix: S8
Typl!: SlIIIO
Parlmeter
....-............-...-.....--.-
Total Organic Cnrbon (HG/KG)
Cation Exchange Cnpnclty (HEO/l)
UK-SDHU04-1J.5 08/10/90
16000.
O.
.......-...-.-.-..-.----..-
~/
II/
ANALYTICAL DATA REPORT
Uoodstock landfill RI/fS
Uoodstock. Illinois
UK'SDHU05-22 08/01/90
............-.---..-.----..
UK'SBHU06-08.5 07/J1/90
16000.
5.88
~/
/
1'0.
O.
-----.......... ..... ........-......-....
/
II/
2
UK-S8HU06-JJ.5 07/J1/90
16000.
O.
..-....................... --.. -............
~/
II/
lIote: (1) lIe5111 ts nre rt'j)Orleil ~i Ih fllInll 1 icrs (I nhorntory Ounll fler/Doto Vall(lnt Ion 01/01 if ICI") to thc ri!Jht 01 Ihe voll/C.
. c'
. I.
-------
-
,.W~N
.'A,it.~~...:-:,. .:-:;
LllORA TOR Y RESt"'L TS
'YOLi\TILE ORGA..~"1C REPORT
Project: Woodstock L:1::c:fill
Project #: 6077€.3~
Locatioa: Woodstock, Illi'1ois
Date Sampled: 7/19/91
Method Detection 3006.001 :3 006.002 :3006.CS~C()
(Yir.h:l~J
607i5.3~:.b
"'"
-
-------
""
LEACHATE WElLS
<
".
-------
, "
I l ~
ANALYTICAL DATA REPORT
Uoodstock Lendflll Rl/fS
Uoodstock, IIlInol s
Hetrlx: LEC Type: tNO Hfl
Genereted by: CAU
Dete Issued: 10-HAY-91
Peremeter ur-LLfIOI-OI 08/08/90 UK-LLfB07-02 02/07191 UK'lLUOI-01 08/08/90 UK-LLUOI-D2 02/08/91 UK-LLUOI-91 08/08/90
.....--. -............ --.. _..-.....-..- -...... .~............-......_-_..__.._- .......--.........-..--.............- _..--e_..____-....---..---..-. -..-..--.-......-----..------- ......-........-....----------
Alualnuft (UG/l) 50. UI 50. UI 283000. I 951,00. I 170000. I
Ant lmany (UG/l) 50. UN/R 5. UN/R 50. UN/R 5. UN/R 50. UN/R
Arsenic (UG/L) 2. UN/R 2. USI 68.8 NS/J 73.7 SI K NS/J
B8rlua (UG/L> 10. UI 10. UI 2600- 1 855. I 21,50. I
Beryillua (UG/L) 5. UI 5. UI 17. I 5. I 12. I
Cecblua (UG/L) 5. UNI 5. UI 36. N/J 6.7 1 35. N/J
Celclua (UG/L) 1000. UI 1000. UI 3020000. I 993000. I 2110000. I
ChrOllllua, totel (UG/L) 10. UI 10. UI 1100. I 306. I 676. I
Cabal t (UG/L) 10. UI 10. UI 415. I 95. I 251. I
Copper (UG/L) 10. UI 10. UI 3070. 1 1080. I .1990. I
Iron (UG/l) 20. UI 192. I 85/000. I 263000. I 572000. I
Leed (UG/L> 3. UI 3. UI 2030. I '96. SI 1220. I
Hegnesfum (UG/l) 1000. UI 1000. UI 1470000. I 456000. I 9/5000. I
Mangenese (UG/L) 10. UI 15. UI 181,00. I 5/00. I 15800. I
Mercury (UG/L) 0.2 UI 0.2 UI 5.3 1 2.2 I 3.2 I
Nickel (UG/L> 20. UI 20. U/ 3090. I 1070. I 20/0. I
Potes. h... (UG/L) 100. UI 100. U/ 62800. I 23200. I 1,7300. I
Selenlua (UG/L) 2. UN/UJ 2. USI 20.6 NS/J 20. USI 10. NS/J
Sliver (UG/L> 10. UN/UJ 10. U"I 23. N/J 20. "1 17. N/J
Sodh.. (UG/L> 1000. UNI 1000. UI 18700. N/J 13000. I 14600. N/J
Thallium (UG/l) 3. UNS/UJ 3. u/ 15.3 NS/J 8.2 KSI 12.9 NS/J
Venedh... (UG/l) 50. UI 50. U/ 1320. I 31,9. I 928. I
Zinc (UG/L> 23. 1 10. U/ 31100. I 131,00. 1 20300. I
Cyenlde (UG/L) 10. UI 10. U/ 60. I 10. UI 37. I
Alkalinity, Totel (HG/L) 5. UI 5. UI 630. IJ 585. I 60. /J
Chiorlde (HG/l) 1. UI 1. U/ 8. I H. I 9. I
Chemical O.ygen Oemand (HG/L) 20. UI 20. U/ 2820. / 38. I 3"0. I
Nltr8tetNltrite Nitrogen (HG/L) 0.06 "1 0.07 I 0.26 "/U 0.02 UI 0.17 "/U
Nitrogen, Ammonle (HG/L) 0.1 UI 0.12 / 15.5 / 11,.2 I 17.1, I
Nitrogen, Totel Kjeldehl (HG/L) 0.1 U/UJ 0.21 I 54.1 IJ 19.8 I 60. IJ
Phosphorus, Totel (HG/L) 0.02 U/UJ 0.02 UI 10. IJ 0.58 I 10.4 /J
Sui fete (HG/L) 5. UI 5. UNI 29. I 53. . N/J 31. I
Totel Dissolved Solids (HG/L) 20. UI 20. UI 612. I 608- I 601,. I
Note: (I) Results Are reported with qualifiers (lal>oratory Qualifier/Data Validation Qualifier) to the right of the value.
-------
ANALYTICAL DATA REPORT 2
Uoodstock landfill Rl/fS
Uood5tock, 1IIInol5
Hetrlx: LEC Type: IND HTL
Per_ter UK-LLU02-01 08/08/90 UK-LLU02-02 02/07/91 UK-LlU02-92 02/07/91 UK-llU03-01 08/08/90 UK-llUO]-O? 02/08/91
"''''''''.-'''''''' --...-....... -............. ."''''''''''''''''' .... -......._-- -- ----.................- .........--..........-.................--..-.. ........ --..- -- ............... "----"'''' ---- ........... --...............--......... "'''''''''''''''''' -.......---.........
Alumll\U1\ (UG/L) 22800. / 54500. / 54800. / 190000. I 9~500. I
Ant Imnv (UG/U 50. UN/R 5. UN/R 5. UN/R 50. UN/R 30. ICN/J
Arsenic (UG/l) 55.5 N/J 88.8 SI 89.5 S/ 50. UN/R 102. S/
8ullm (UG/l) 810. / 1250. I 1360. I 10800. I 5900. /
Berylt lum WG/L> 5. U/ 5. UI 5. U/ 9. / 5.5 I
Cechlum WG/l) 5. UNI 6.3 I 8.2 I 3]]. N/J 121. I
Celclum (UG/l) 476000. / 768000. / 913000. I 3080000. / 1240000. I
Chromium, tote I (UG/l) 86. / 153. I 151. I 1400. I 799. I
Cobal t (UG/L) 60. / 66. I 62. I 227. I 19. I
Copper (UG/l) 497. / 1030. I 972. I 10800. I 7120. I
Iron (UG/l) 262000. / 485000. I 501000. I 946000. I 45~000. I
Leed (UG/L) 150. I 330. 51 429. 51 18000. I 12900. SI
Hegneslum (UG/L) 171.000. / 332000. I 374000. I ~27000. I ]] 7000. I
Hanganese (UG/l) 7980. / 15000. I 16900. I 26500. I 13000. I
Hercury (UG/L) 0.28 / 1.2 I 0.95 I 5.7 I 3.7 I
Nlctel (UG/L) 1950. / 4390. I 4300. I 15000. I 8090- I
Potesslum (UG/l) 28000. / 26500. I 26100. I 177000. / 135000. I
SelenIum WG/l) 10. UNS/UJ 2. USI 2. USI 13.5 NS/J 20. USI
Sliver (UG/L) 10. UN/UJ 10. U.' 10. U.' 58. N/J 29.5 .1
SodIum (UG/l) 22700. N/J 32100. I 33300. I 205000. N/J 215000. I
Th8lt lum (UG/l) 5. ICNS/J 6.7 KSI 9. ICSI 8.8 ICNS/J ~.4 ICSI
V8n8dlum (UG/l) 108. / 1011. I 94. I 503. I 275. I
llnc (UG/l) 8140. / 17100. I 16800. I 185000. I 93600. I
Cvenlde (UG/L) 20. / 18. / 33. I 50. I 42. /
Altatlnlty. Tot81 (HG/L) 907. /J 973. I 934. / 1510. IJ 1900. I
Chtorlde (HG/l) 29. / 38. I 34. I 156. I 159. I
Chemical Oxygen Demand (HG/l) 381. / 125. I 117. / 6970. I 197. /
Nltrate+Nltrlte Nitrogen (HG/l) 0.18 */U 0.04 IU 0.02 UI 0.04 U.' 0.02 III
Nitrogen, Ammoni8 (HG/L) 21,.9 / 25.2 I 28.4 I 27.1 I 51.8 I
Nitrogen, Total ICleldehl (HG/l) 21.7 /J 36.5 I 41. I 1610. IJ 169. I
Phosphorus, 10tel (HG/L) 2.31, /J 5.96 I 6.54 I 23.2 IJ 16.1 I
Sulf8te (HG/l) 10. I 43. N/J 33. N/J 37. I 35. N/J
Tot81 Dissolved Solids (HG/l) 924. I 918. I 904. I 1630. I 1570. I
Note: (1) Results are reported with qualifiers (l~borntory Qualifier/Date Validation Qualifier) to the right of the value.
Q ;)
, 'I
-------
. "
, l:
ANALYTICAL DATA REPORT 3
lIoodstock lendf \I I Al/fS
Uoodstock, Illinois
Hatrlx: LEC Type: IND Hfl
Parameter IIK-llII04-01 08/08/90 IIK-llII04-02 02/08/91 lIK-llIlO5-01 08/08/90 WK-llII05-02 02/08/91
....-------------.--.--.------ _....__a........... --............ ...--............ ------------------------ -----.-e--____-----....--- ------------...-----------
Alumlnun (UG/l) 174000. I 97000. I 167000. I 358000. I
Antimony (UG/l) 50. UN/R 5. UN/R 50. UN/R 5. UNS/R
Arsenic (UG/L) 50, UN/R 76.5 51 2. UN/R 2.9 KSI
B8rlum (UG/l) 2070. I 1130. I 4420. I 2070. I
Beryllium (UG/I.) 9. I 5. I 10. I 23.5 I
Cadnlun (UG/L> 21. N/J 5. UI 19. N/J 32. I
Calcium (UG/L) 1700000. I 919000. I 3460000. I 4390000. I
Chromium, total (UG/L) 548. I 250. I 629. I 1200. I
Cobal t (UG/l) 255. I 117. I 261. I 546. I
Copper WG/L) 2160. I 1060. I 1900. I 4480. I
Iron (UG/l) 742000. I 350000. I 773000. I 1560000. I
leed (UG/l) 1900. I 982. 51 950. I 3. UI
Magnesium (UG/L) 881000. I 405000. I 654000. I 1260000. I
Manganese (UG/L) 15500. I 6330. I 19000. I 31200. I
. Hercury (UG/l) 2.2 I 1.4 I 1.8 I 3.6 I
Nickel (UG/L> 1900. I 846. I 3760. I 5770. I
Potassium (UG/l) 53000. I 27300. I 64300. I 83400. I
Selenium (UG/l) 10. UNS/UJ 3.7 !CSI 15.4 NS/J 9.5 SI
Sliver (UG/l) 10. UN/UJ 10. UAI 12. N/J 10. UAI
Sodlllll (UG/L) 106000. N/J 115000. I 66200. N/J 93500. I
Thallium (UG/l) 12_4 NS/J 4.2 KSI 12.5 NS/J 5.3 KSI
Vanadium (UG/L) 676. I 28J. I 576. I 1180. I
Zinc (UG/l) 16700. I 8700. I 8340. I 16800. I
Cyanide (UG/L> 25. I 10. UI 58. I 29. I
Alkalinity, Total (MG/l) 876. IJ 951. I 859. IJ 1100. I
Chloride (MG/L) 121. I 127. I 40. I 34. I
Ch~lc.1 Oxygen Demand (HG/L) 2260. I 99. I 7I1JO. I 150. I
NltratetNltrlte NItrogen (HG/L) 0.2 A/U 0.02 UI 0.15 A/U 0.02 UI
NItrogen, AmmonIa (HG/L) 7.55 I 3.46 I 31.9 I 32_3 I
NItrogen, Total !Cjeldahl (HG/l) 26.2 IJ 19.6 I 124. IJ 120. I
Phosphorus, Total (MG/L) 7.48 IJ 5.65 I 12.2 IJ 9.4 I
Sulfate (MG/l) 29. I 31. N/J 9. I 34. N/J
Total Dissolved SolIds (HG/l) 1010. I 1060. I 904. I 1052. I
Note: (1) Results are reported with qualifiers (lnl~rotory Qualifier/Data Validation QualIfier) to the right 0' the value.
-------
ANALYTICAL DATA REPORT
Uoods tock landf III RI/FS
Uoodstock, III inols
Matrl x: lEC Type: PPCB
Generated by: CAU
Oete Issued: 10-MAY.91
Plremeter wr'llFB01-01 08/08/90 WK-llU01-01 08/08/90 WK-llU01.91 08/08/90 UK'llU02-01 08/08/90 UK-llUOJ-01 08/08/90
----.------------------------- .-.----.--.------------- ------------------------ ------------------------ ------------------------ ------------.----.------
alpha-SHC CUG/l) 0.05 UI 0.05 UI 0.05 U/ 0.05 UI 0.05 U/
bete'SHC (UG/l) 0_05 UI 0.05 U/ 0.05 U/ 0.05 U/ 0.05 U/
delta-SHC (UG/l) 0.05 ul 0.05 U/ 0.05 U/ 0.05 U/ 0.05 III
gemme-SHC (lindane) (UG/l) 0.05 UI 0.05 U/ 0.05 U/ 0.05 U/ 0.05
Heptachlor (UG/l) 0.05 UI 0.05 U/ 0.05 U/ 0.05 U/ 0.05 IJ/
Aldrin WG/l) 0.05 UI 0.05 U/ 0.05 U/ 0.05 U/ 0.05 UI
Heptachlor epoxide (UG/l) 0.05 UI 0.05 U/ 0.05 UI 0.05 U/ 0.05 UI
fndosulfan I (UG/l) 0.05 UI 0.05 U/ 0.05 U/ 0.05 U/ 0.05 II/
Dieldrin (UC/l) 0.1 lJl 0.1 U/ 0.1 U/ 0.1 U/ 0.1 U/
4,4'-00E CUG/l) 0.1 UI 0.1 UI 0.1 U/ 0.1 U/ 0.1 IJI
fndrln (UG/l) 0.1 UI 0.1 U/ 0.1 UI 0.1 U/ 0.1 UI
fndosulfen II (UC/l) 0.1 UI 0.1 UI 0.1 UI 0.1 UI 0.1 U/
4,4'-000 (UG/l) 0.1 UI 0.1 UI 0.1 UI 0.1 UI 0.1 U/
Endolulf8n lulfate (UG/l) 0.1 ul 0.1 U/ 0.1 UI 0.1 u/ 0.1 III
4,4'-00T (UG/l) 0.1 UI 0.1 UI 0.1 U/ 0.1 UI 0.1 IJ/
Methoxychlor (UG/l) 0.5 lJl 0.5 UI 0.5 U/ 0.5 UI 0.5 UI
fndrln ketone (UC/l) 0.1 lJl 0.1 U/ 0.1 UI 0.1 UI 0.1 U/
alpha-Chlordane (UC/l) 0.5 lJl 0.5 U/ 0.5 U/ 0.5 UI 0.5 UI
gemme-Chlordane (UG/l) 0.5 lJl 0.5 UI 0.5 UI 0.5 u/ 0.5 III
Toxaphene (UG/l) 1. UI 1. UI 1. U/ 1. U/ 1. U/
Aroclor-1016 (UC/l) 0.5 UI 0.5 UI 0.5 U/ 0.5 U/ 0.5 lI/
Aroclor-1221 (UG/l) 0.5 UI 0.5 UI 0.5 UI 0.5 U/ 0.5 UI
Aroctor-1232 (UG/l) 0.5 UI 0.5 U/ 0.5 U/ 0.5 U/ 0.5 u/
Aroclor-1242 (UG/l) 0.5 UI 0.5 UI 0.5 UI 0.5 U/ 0.5 UI
Aroclor-1248 (UC/l) 0.5 UI 0.5 UI 0.5 U/ 0.5 U/ 0.5 UI
Aroclor'1254 (UG/l) 1. UI 1. UI 1. U/ 1. UI 1. U/
Aroclor.1260 (Wi:1 J 1. UI 1. UI 1. U/ 1. u/ 1. UI
Note: (1) Rrsllits ore reported with qualifiers (laboratory Quolifier/Date Validation Qualifier) to the right of the vol III'.
-------
I I'.~
, \-
ANALYTICAL DATA REPORT 2
Uoodstock land' III R IIFS
Uoodstock, Illinois
Hatrix: lEC Type: PPCB
Parameter UK-llU04-01 08/08/90 UK-llU05-01 08/08/90
..............-............... ........................ ........... ............. -......
alpha-RHC (UG/l) 0.05 U/ 0.05 U/
beta'IHC (UG/l) 0.05 U/ 0.05 U/
delta-8HC (UG/L) 0.05 U/ 0.05 U/
gamma.8HC (lindane) (UG/l) 0.05 U/ 0.05 U/
Heptachlor (UG/l) 0.05 U/ 0.05 U/
AldrIn (UG/L) 0.05 U/ 0.05 U/
Heptachlor epoKlde (UG/l) 0.05 U/ 0.05 U/
Endosul'an I (UG/l) .0.05 U/ 0.05 U/
DIeldrin (UG/l) 0.1 U/ 0.1 U/
4,4"'00E (UG/l) 0.1 U/ 0.1 U/
Endrln (UG/l) 0.1 U/ 0.1 U/
Endosulfan II (UG/l) 0.1 U/ 0.1 U/
4,4"-000 (UG/L) 0.1 U/ 0.1 U/
Endosulfan sulfate (UG/l) 0.1 U/ 0.1 U/
4,4 I 'OOT (UG/l) 0.1 U/ 0.1 U/
Hethoxychlor (UG/l) 0.5 U/ 0.5 U/
Endrln ketone (UG/l) 0.1 U/ 0.1 U/
.Iph.-Chlordane (UG/l) 0.5 U/ 0.5 U/
Gamme-Chlordane (UG/l) 0.5 U/ 0.5 U/
Toxaphene (UG/l) 1. U/ 1. U/
Aroclor'1016 (UG/l) 0.5 U/ 0.5 U/
Aroclor-1221 (UG/l) 0.5 U/ 0.5 U/
Aroclor.1232 (UG/l) 0.5 U/ 0.5 U/
Aroclor-1242 (UG/l) 0.5 U/ 0.5 U/
Aroclor'1248 (UG/l) 0.5 U/ 0.5 U/
Aroclor'1254 (UG/l) 1. U/ 1. U/
Aroclor.1260 (UG/l) 1. U/ 1. U/
Note: (II Results an! reported with qualifiers (laboratory Qualifier/Data Validation Qualifier) to the right 0' the value.
-------
ANALYTICAL DATA REPORT
Uoodstock landfill Rl/fS
Uoodstock, I It Inols
Matrix: lEC Type: VOt
Generated by: CAU
Date Issued: 10-MAY'91
Parameter WK-llfBOI-OI 08/08/90 UK-llfB01-02 02/07191 UK-llTBOZ-OI 08/08/90 UK-llT80J-01 08/08/90 UK-llT807-02 02/08/91
------..... ----.......... -..---.. --............. ---.-.-....------------..-- -------..-----.....----..-- ..-- ............ .......-....... ----....... ...-----..-..----..-.-.........-- ..................-...............---.
Chloromethane (UG/l) 10. UI 10. UI 10. UI 10. UI 10. UI
Bromomethane (UG/l) 10. U/ 10. U/ 10. U/ 10. UI 10. UI
Vinyl chloride (UG/l) 10. U/ 10. U/ 10. U/ 10. UI 10. UI
Chloroethane (IIG/l) 10. UI 10. UI 10. UI 10. UI 10. U/
Methylene chloride (UG/l) 10. UI 5. U/ 5. UI 1J. B/U 5. UI
Acetone (UG/l) 10. U/ 10. U/ 10. U/ 10. UI 10. UI
Carbon disulfide (IIG/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. III
1,1-0fchloroethene (IIG/l) 5. U/ 5. U/ 5. III 5. III 5. III
1,1-0Ichloroethane (IIG/l) 5. UI 5. U/ 5. III 5. III 5. III
1.2'Olchloroethene (total) (UG/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. III
Chlorofor. (UG/l) 5. UI 5. U/ 5. U/ 5. U/ 5. II/
1,2'Ofchloroethane (UG/l) 5. UI 5. U/ 5. UI 5. U/ 5. UI
2-8utlnone (UG/l) 10. UI 10. U/ 10. III 10. UI 10. III
1,1,I-Trlchloroethane (UG/l) 5. UI 5. U/ 5. III 5. III 5. UI
Carbon tetrachloride (UG/l) 5. IJI 5. UI 5. UI 5. UI 5. III
Vinyl acetate (UG/l) 10. III 10. UI 10. UI 10. U/ 10. U/
8romodlchloromethane (UG/l) 5. UI 5. U/ 5. UI 5. UI 5. III
1,2'Olchloropropane (UG/l) 5. UI 5. UI 5. II/ 5. UI 5. UI
cls-I,3-0Ichloropropene (UG/l) 5. UI 5. UI 5. U/ 5. U/ 5. UI
Trlchloroethene (Will) 5. UI 5. UI 5. UI 5. UI 5. U/
Dlbromochloromethane (UG/l) 5. UI 5. U/ 5. UI 5. UI 5. III
1,1,2-Trlchloroethane (UG/l) 5. UI 5. U/ 5. UI 5. UI 5. UI
8enzene (UG/l) 5. U/ 5. U/ 5. UI 5. III 5. UI
trans-1,J-Dlchloropropene (UG/l) 5. III 5. II/ 5. II/ 5. UI 5. UI
Bromoform (UG/l) 5. . III 5. UI 5. UI 5. III 5. III
4-"ethyl-2-~ntanone (UG/l) 10. U/ 10. III 10. III 10. III 10. UI
2-Hexanone (UG/l) 10. III 10. U/ 10. UI 10... II/ 10. III
Tetrachloroethene (UG/l) 5. III 5. UI 5. U/ 5. UI 5. UI
1,1,2,2-Tetrachloroethane (UG/l) 5. U/ 5. II/ 5. III 5. III 5. III
Toluene (UG/L> 5. UI 5. II/ 5. III 5. III 5. III
Chlorobenzene (UG/l) 5. III 5. II/ 5. UI 5. III 5. III
Ethylbenrene (IIG/l) 5. U/ 5. II/ 5. UI 5. III 5. III
Styrene (IIG/l) 5. III 5. III 5. III 5. III 5. III
Xylenes (total) (UG/l) 5. UI 5. U/ 5. U/ 5. III 5. III
Note: (I) Results Are reported with qualifiers (l/lhoratory Qualifier/Data Validation Ouallfler> to the right of the value.
. ,~
I ~ ~
-------
(;1 ~~
I .~ -
ANALYTICAL DATA REPORT 2
woodstock Landfill RIIFS
Woodstock, III inois
Matrix: IEC Type: VOC
Parameter UK-IIW01-01 08/08/90 WK-IIW01-02 02/08/91 UK-IlUD1-91 08/08/90 ~-llW02-01 08/08/90 UK-IIW02-02 02/07/91
.....-...--....... --- -----..- --.......... -.----....-----.........a.- .a...a._........-..._...a---_. .. _.....a a.. -. -- -.. -. _..a..... - ...a___..._-...-..-.-............ .. -....... a.. . .. . . . - - - .. .... -.. ..
Chloromethane (UG/I) 10. U/ 10. U/ 10. U/ 10. U/ 10. U/
Bromomethane (UG/I) 10. U/ 10. U/ 10. U/ 10. U/ 10. u/
Vinyl chloride (UG/I) 10. U/ 10. U/ 10. U/ 10. U/ 10. U/
Chloroethane (UG/l) 10. U/ 10. U/ 10. U/ 10. U/ 10. U/
Methylene chloride (UG/I) 5. U/ 5. U/ 5. U/ 5. U/ 5. II/
Acetone (UG/I) 10. UI 10. U/ 10. II/ 10. U/ 10. HI
Carbon disulfide (UG/I) 5. II/ 5. II/ 5. U/ 5. U/ 5. HI
1,1-0Ichloroethene (UG/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. U/
1,1-0Ichloroethane (UG/L) 5. U/ 5. U/ 5. U/ 5. U/ 5. H/
1,Z-Olchloroethene (total) (UG/l) 5. U/ 16. / 5. U/ 5. U/ 5. U/
Chloroform (UG/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. u/
1,2-0ichloroethane (UG/I) 5. U/ 5. U/ 5. U/ 5. U/ 5. II/
Z-Butanone (UG/l) 10. u/ 10. II/ 10. II/ 10. II/ 10. III
1,1,1-Trlchloroethane (IIG/l) 5. II/ 5. II/ 5. II/ 5. u/ 5- II/
Carbon tetrachloride (UG/I) 5. U/ 5. U/ 5. U/ 5. U/ 5. II/
Vinyl acetate (UG/I) 10. U/ 10. U/ 10- U/ 10. U/ 10- U/
Bromodlchloromethane (UG/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. U/
1,2-0Ichloropropene (UG/I) 5. U/ 5. U/ 5. U/ 5. U/ 5. II/
cla'1,3-0Ichloropropene (UG/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. U/
Trlchloroethene (UG/I) 5. U/ 5. U/ 5. U/ 5. U/ 5. U/
Olbromochloromethane (IIG/I) 5. U/ 5. U/ 5. UI 5. U/ 5. II/
1,1,2-Trlchloroethane (UG/I) 5. U/ 5. U/ 5. U/ 5. U/ 5. U/
Benzene (UG/l) 9. / 11. / 8. / II. / 9. /
trans-1,3-Dlchloropropene (UG/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. U/
Bromoform (IIG/l) 5. II/ 5. II/ 5. U/ 5. U/ 5. II/
"Methyl-2'pentanone (UG/I) 10. II/ 10. U/ 10. U/ 10. U/ 10. II/
2'Hexaoone (UG/l) 10. II/ 10. U/ 10. II/ 10- U/ 10. II/
Tetrachloroethene (IIG/l) 5. II/ 5. II/ 5. II/ 5. U/ 5. II/
1,I,2,Z-Tetrachloroethane (IIG/l) 5. II/ 5. U/ 5. U/ 5.. U/ 5. U/
Toluene (UG/l) 1. J/ 5. U/ ,. J/ 1. J/ 5. U/
Chlorobenzene (UG/l) 3. J/ 8. / 3. J/ 6. / II. /
Ethylbenzene (UG/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. II/
Styrene (UG/l) 5. U/ 5. U/ 5. U/ 5. U/ 5. U/
Xylenes (total) (UG/l) 2. J/ 8. / 2. J/ 5. / 7. /
Note: (1) Results lire reported with qualifiers (lahoratory Qualifier/OeU Validation Qualifier) to the right of the value.
-------
ANAlYllCAl OATA REPORT J
Uoodstock landfill R /lfS
Uoodstock, Itllnols
Matrix: LEC Type: VOC
Parameter UK-LlU02-92 02/07/91 UK-llU03-01 08/08/90 UK-llUOJ.02 02/08/91 UK-llU04-01 08/08/90 UK-lLU04.0202/08/91
-..---------.......-------------- --..- ---- -...... -- -....-............ .----------..-..---------- ........---.. ---.. -...---..... ----- ...... -- ---.. ---.... "'.. -............... .. .. .. .. .......... .. .... ........ ................
Chloromethane (UG/l) 10. UI 10. UI 10. UI 10. UI 10. III
Bromomethane (tlG/l) 10. III 10. UI 10. UI 10. UI 10. III
Vlnvl chloride (UG/l) 10. UI 10. IJ/ 10. UI 10. U/ 10. U/
Chloroethane (UG/l) 10. UI 10. UI 10. UI 10. UI 10. UI
Methvlene chloride (UG/l) 7. B/U 5. UI 5. UI 5. UI 5. LJI
Acetone WG/l) 10. UI 10. UI 10. U/ 10. UI 10. UI
Carbon disulfide (UG/l) 5. UI 5. UI 5. UI 5. UI 5. U/
1,1.0Ichloroethene (UG/l) 5. UI 5. UI 5. UI 5. UI 5. UI
1,1-0Ichloroethane (UG/l) 5. UI 5. UI 5. UI 5. UI 5. UI
1,2'Olchloroethene (total) (UG/l) 5. UI 5. UI 5. UI 5. UI 5. UI
Chloroform (UG/l) 5. UI 5. UI 5. U/ 5. U/ 5. UI
1,2-0Ichloroethane (UG/l) 5. UI 5. U/ 5. UI 5. UI 5. U/
2-Butanone (UG/l) 10. UI 10. UI 10. UI 10. UI 10. UI
1,1,I-Trlchloroethane (UG/l) 5. UI 5. UI 5. UI 5. UI 5. tll
Carbon tetrachloride (UG/l) 5. UI 5. U/ 5. UI 5. UI 5. UI
Vlnvl acetate (UG/l) 10. UI 10. U/ 10. UI 10. UI 10. U/
Bromadlchloromethane (UG/l) 5. UI 5. UI 5. UI 5. UI 5. UI
I,Z-Dlchloropropane (UG/l) 5. UI 5. UI 5. UI 5. UI 5. U/
cla'I,3-0Ichloropropene (UG/l) 5. UI 5. U/ 5. UI 5. UI 5. UI
Trfchloroethene (UG/l) 5. UI 5. UI 5. UI 5. UI 5. UI
Olbromochloromethane (UG/l) 5. UI 5. UI 5. UI 5. UI 5. UI
1,1,2'Trlchloroethane (UG/l) 5. UI 5. UI 5. UI 5. UI 5. u/
Benzene (UG/l) 9. I 3. J/ 3. JI 5. UI 5. tll
trans-I,3-Dlchloropropene (UG/l) 5. UI 5. u/ 5. UI 5. U/ 5. tll
Bromoform (UG/l) 5. 01 5. UI 5. U/ 5. UI 5. UI
4-Hethyl-2.pentanone (UG/l) 10. UI 10. UI 10. UI 10. U/ 10. tI/
2-Hexanone (UG/l) 10. UI 10. U/ 10. UI 10. UI 10. UI
Tetrachloroethene (UC/l) 5. UI 5. UI 5. UI 5. UI 5. UI
1,1,2,2'Tetrachloroethane (UG/l) 5. 01 5. U/ 5. UI 5. UI 5. U/
Toluene (UG/l) 5. UI 5. UI 5. tll 5. UI 5. UI
Chlorobenzene (UG/l) 8. / 5. UI 5. U/ 5. U/ 5. UI
Ethvlbenzene (UC/l) 5. U/ 5. UI 5. UI 5. U/ 5. U/
Styrene (UG/l) 5. UI 5. UI 5. U/ 5. U/ 5. UI
Xylenes (total) (UG/l) 6. / 5. U/ 5. U/ 5. U/ 5. U/
Note: (1) Results are reported with qualifiers (I ..horatory QualifierlData Validation Qualifier) to the right of the vallie.
::. t':
j .4 b
-------
, c
I 't'
ANALYTICAL DATA REPORT I,
"oods t od landf I II RI/fS
"oDdst oc k, IIIInol5
Hatrlx: lEC Type: VOC
Parameter ~-ll"05-01 08/08/90 ~-ll"05-02 02/08/91
....--........ .................- --... ---.............. --..---.....---"---""'''---- ... -...-....._......... -- --....... ---.......
ChloromethAne (UG/l) 10. III 10. III
Bromomethane (UG/l) 10, III 10. UI
Vinyl chloride (UG/l) 10. III 10. UI
Chloroethane (UG/l) 10. UI 10. UI
Hethylene chloride (UG/l) 5. UI 5. UI
Acetone (UG/l) 10. UI 10. UI
Carbon disulfide (UC/l) 5. UI 5- UI
1,1-0lchloroethene (UG/l) 5. UI 5. UI
1,1-0lchloroethane (IIG/l) 5. UI 5. UI
1,Z-Olchloroethene (total) (UG/l) 5. UI 5. UI
Chloroform (UG/l) 5. UI 5. UI
1,Z-Olchloroethane (UG/l) 5. UI 5. UI
Z-Butanone (IIG/l) 10. III 10. UI
1,1,1-Trlchloroethane (IIG/l) 5. UI 5. UI
Carbon tetrachloride (UG/l) 5. III 5. UI
Vinyl acetate (UG/l) 10. III 10. UI
Bromodlchloromethane (IIG/l) 5. UI 5. UI
1,Z'Olchloropropane (IIG/l) 5. III 5. UI
cl.-1~3-Dlchloropropene (UC/l) 5. UI 5. UI
Trlchloroethene (IIG/l) 5. UI 5. UI
Dlbromochloromethane (UG/l) 5. UI 5. UI
1,1,Z-Trlchloroethane (UG/l) 5. UI 5. UI
Benrene (UG/l) 11. I 11,. I
trans.1,]-Dlchloropropene (UG/l) 5. III 5. UI
Bromoform (UG/l) 5. UI 5. UI
I,-Methyl-Z-pentanone (UG/l) 10. III 10. UI
2-Hexanone (IIG/l) 10. UI 10. UI
Tetrachloroethene (UG/l) 5. UI 5. UI
1,1,Z,Z-Tetrachloroethane (UG/l) 5. III 5. UI
Toluene (UC/l) 2. JI 5. UI
Chlorobenrene (UG/l) 8. I 7. I
Ethylbenrene (IIG/l) 5. UI 5. UI
Styrene (UG/l) 5. UI 5. UI
Xylenes (total) (IIG/l) 2. JI 2. JI
Note: (I) Results /Ire reported with qualifiers (laboratory Qualifier/Data Validation Qualifier> to the right 01 the value.
-------
ANALYTICAL DATA REPORT
Uoodstock landfill RI/FS
Uoodstock. I I I inois
Hatrlx: lEC Type: SVOC
Generated by: CAU
Date Issued: 10-HAY-91
Perameter
UK-LlFBOI-OI 08/08/90
UK-LLFB07-02 02/07/91
UK-LLUOI-01 08/08/90
UK-LLUOI-91 08/08/90
UK-lLU02-01 08/08/90
................---------..---
...---.-----------------
------------------------
........--.....- ---... ----- ---- ---
... --- ---------------- ----
.............. ........ .. .. .... ...... .. ......... .. ..
Phenol (UG/l) 10. U/ 20. II/ 10. II/ 10. II/ 10. II/R
bls(2-Chloroethyl) ether (UG/L) 10. U/ 20. U/ 10. II/ 10. II/ 10. II/R
2-Chlorophenol (IIG/L) 10. U/ 20. II/ 10. II/ 10. II/ 10. II/R ~
'.3-Dlchlorobenzene (IIG/l) 10. II/ 20. II/ 10. II/ 10. II/ 10. II/R
. 1,r.-Dlchlorobenzene (IIG/L) 10. II/ 20. II/ 2. J/ 10. II/ 2- J/J
Benzyl Alcohol (IIG/l) 10. II/ 20. II/ 10. II/ 10. II/ 10- II/R
'.2-Dlchlorobenzene (IIG/l) 10. II/ 20. U/ 10. U/ 10. U/ 10- II/R
2-Hethylphenol (UG/l) 10. II/ 20. U/ 10. II/ 10. U/ 10. II/R
bls(2-Chlorolsopropyl)ether (IIG/L) 10. II/ 20. II/ 10. II/ 10. II/ 10. II/R
4-Methylphenol (IIG/L) 10. II/ 20. II/ 10. II/ 10. II/ 10. II/R
N-Nltroso-di-n-dlpropylamine (IIG/l) 10. II/ 20. II/ 10. II/ 10. II/ 10. II/R
Hexachloroethane (UG/l) 10. II/ 20. U/ 10. II/ 10. II/ 10. II/R
Nitrobenzene (UG/L) 10. II/ 20. II/ 10. II/ 10. U/ 10. II/R
Isophorone (UG/l) 10. U/ 20. U/ 10. II/ 10. II/ 10. II/R
2-Nltrophenol (UC/l) 10. U/ 20. U/ 10. II/ 10. U/ 10. IIIR
2.r.-Olmethylphenol (IIG/l) 10. II/ 20. II/ 10. U/ 10. U/ 10. IIIR
Benzoic Acid (UG/l) 50. U/ 100. II/ 50. U/ 50. II/ 50. II/R
bls(2-Chloroethoxy)methane (IIG/l) 10. II/ 20. II/ 10. II/ 10. U/ 10. II/R
2,4-0Ichlorophenol (UG/l) 10. II/ 20. ' II/ 10. u/ 10. U/ 10. II/R
1.2,4-Trlchlorobenzene (UG/l) 10. U/ 20. II/ 10. II/ 10. II/ 10. II/R
Naphthalene (IIG/l) 10. U/ 20. II/ 10. II/ 10. II/ 6. J/J
4-Chloroanlllne (UG/l) 10. II/ 20. ' II/ 10. U/ 10. U/ 10. II/R
Hexachlorobutadlene (IIG/l) 10. II/ 20. II/ 10. II/ 10. U/ 10. II/R
4'Chloro-3-methylphenol (IIG/L) 10. II/ 20. II/ 10. II/ 10. U/ 10. II/R
2-Methylnaphthalene (IIC/l) 10. II/ 20. II/ 10. II/ 10. II/ 10. II/R
Hexachlorocyclopentadiene (IIG/l) 10. II/ 20. II/ 10. II/ 10. II/ 10- II/R
2.4.6-Trlchlorophenol (IIG/l) 10. II/ 20. II/ 10. U/ 10. II/ 10. II/R
2.r..5'Trlchlorophenol (IIG/l) 50. II/ 100. II/ 50. II/ 50; II/ 50. II/R
2-Chloronaphthalene (IIG/L) 10. U/ 20. II/ 10. II/ 10. II/ 10. II/R
2-Nltroanlllne (IIG/l) 50. U/ 100. II/ 50. II/ 50. II/ 50. II/R
Dlmethylphthelote (IIC/l) 10. II/ 20. II/ 10. II/ 10. II/ 10. II/R
Acenaphthylene (IIG/l) 10. II/ 20. II/ 10. II/ 10. II/ 10. II/R
2,6-Dinitrotoluene (IIG/L) 10. II/ 20. II/ 10. II/ 10. II/ 10. II/R
3-Nltrooniline (IIC/L) 50. II/ 100. II/ 50. II/ 50. II/ 50. II/R
Acenaphthene (IIG/l) 10. II/ 20. II/ 10. II/ 10. II/ 10. II/R
2.4-Dinitrophenol (IIG/l) 50. II/ 100. II/ 50. II/ 50. II/ 50. II/R
t,'Nltrophenol (IIG/L) 50. II/ 100. U/ 50. II/ 50. II/ 50. II/R
Note: (1) Resul ts are reported wi th 'luaU f iers (Laboratory Ouallfler/Data Validation Ouallfler) to the right of the value.
, "
I ,j t
-------
, ,
, ,
ANALYTICAL DATA REPORT Z
Uoodstock landfill RIIfS
Uoodstock. Illinois
Hatrlx: lEC Jype: SVOC
Parameter UK.llU02-02 02/07/91 UK-llU02-92 02/07/91 UK-llUOJ-OI 08/08/90 UK-llU04-01 08/08/90 UK'llU05-01 08/08/90
-...---..... ---................. --................................ .... ........................... ........ .................... ----..--..-----..-------..-.. --.......................... --........ ---... -- ------------------------ -.. ... ..... ......... - - - ... - ... ........ ... ........... -..
Phenol (UG/l) 20. U/ ZOo U/ 10. U/ 10. U/ 10. U/
bls(2'Chloroethyl) ether (UG/l) 20. U/ 20. U/ 10. U/ 10. U/ 10. U/
2'Chlorophenol (UG/l) 20. U/ 20. U/ 10. U/ 10. U/ 10. II/
1.J-Dlchlorobenzene (UG/l) 20. U/ 20. U/ 10. u/ 10. u/ 10. u/
1,"Dlchlorobenzene (UG/l) 6. J/ 8. J/ 10. U/ 10. u/ Z. J/
Benzyl Alcohol (UG/l) 20. U/ 20. U/ 10. U/ 10. U/ 10. U/
1.2'Olchlorobenzene (UG/l) 20. U/ 20. U/ 10. U/ 10. U/ 10. U/
2'Hethylphenol (UG/l) 20. U/ 20. U/ 10. U/ 10. u/ 10. u/
bls(2-Chlorolsopropyl)ether (UG/l) 20. U/ 20. U/ 10. U/ 10. U/ 10. u/
"Hethylphenol (UG/l) ZOo U/ ZOo 1// 10. U/ 10. U/ Z. J/
N.Nltroso'dl-n'dipropylemine (UG/l) ZOo U/ ZOo U/ 10. U/ 10. U/ 10. U/
Hexachloroethane (UG/l) 20. U/ 20. U/ 10. U/ 10. u/ 10. U/
Nitrobenzene (UG/l) ZOo U/ 20. U/ 10. u/ 10. u/ 10. u/
Isophorone (UG/l) ZOo U/ ZOo U/ 10. U/ 10. U/ 10. U/
2-Nltrophenol (UG/l) 20. U/ 20. U/ 10. U/ 10. 1// 10. U/
2.'-Dlmethylphenol (UG/l) 20. u/ 20. U/ 10. u/ 10. u/ 10. u/
Benzoic Acid (UG/l) 100. u/ 100. U/ 54. 9/J 10. u/ Z8. BJ/J
bls(2-ChloroethoKy)methene (UG/l) 20. U/ ZOo U/ 10. U/ 10. U/ 10. U/
2."Dlchlorophenol (UG/l) 20. U/ 20. U/ 10. U/ 10. U/ 10. 11/
'.2."Trlchlorobenzene (UG/l) 20. u/ 20. U/ 10. u/ 10. U/ 10. U/
Naphthalene (UG/l) 26. / ]'. / 10. U/ 10. U/ 10. U/
4-Chloroanlllne (UG/l) ZOo U/ 20. U/ 10. U/ 10. U/ 10. U/
HeKlchlorobutadlene (UG/l) 20. U/ 20. U/ 10. U/ 10. U/ 10. U/
"Chloro-]'methylphenol (UG/l) 20. U/ 20. U/ 10. U/ 10. U/ 10. U/
2-Hethylnaphthalene (UG/l) 20. U/ 20. U/ 10. U/ 10. U/ 10. U/
HeKlchlorocyclopentadlene (UG/l) 20. 11/ 20. U/ 10. U/ 10. U/ 10. u/
2.4,6'Trlchlorophenol (UG/l) 20. U/ 20. U/ 10. U/ 10. U/ 10. U/
2,4,5-Jrlchlorophenol (UG/l) 100. u/ 100. U/ 50. U/ 50. U/ 50. U/
2'Chloronaphthalene (UG/l) 20. U/ 20. U/ 10. U/ u,. U/ 10. II/
2-Nltroanlllne (UG/l) 100. U/ 100. U/ 50. U/ 50. U/ 50. U/
Dlmethylphthalate (UG/l) 20. u/ 20. U/ 10. U/ 10. UI 10. 11/
Acenaphthylene (UG/l) ZOo U/ 20. U/ 10. U/ 10. U/ 10. u/
2.6-Dlnltrotoluene (UG/l) 20. II/ 20. U/ 10. U/ 10. U/ 10. 11/
]'Nltroanlllne (UG/l) 100. U/ 100. U/ 50. U/ 50. u/ 50. U/
Acenephthene (UG/l) ZOo II/ ZOo U/ 10. U/ 10. I U/ 10. 1//
2.4-0Initrophenol (I/G/l) 100. U/ 100. U/ 50. U/ 50. U/ 50. 11/
'-Nltrophenol (UG/l) 100. U/ 100. U/ 50. u/ 50. U/ 50. II/
Note: (1) Results are reported with quolifiers (lAboratory Qualifler/Oete Validation Qualifier) to the right 01 the value.
-------
ANALYTICAL DATA REPORT ]
Woodstock landfitl R !lfS
Uoodstock, illinois
Matrix: lEC Type: SVOC
Paremeter UK-llfBOI-01 08/08/90 UK-llfB07-02 02/07/91 UK-llUOI-01 08/08/90 UK-llWOI-91 08/08/90 UK -ll U02 - 0 1 08/08190
.......-- ........- ........... -.. ..--......... --.. --.... --------.---------..........-- -----------------..-...---- ......... -- --....... --...-...... -- --- -- ......--.. --.. -"'. ....... ...-........... ............ ......... .. .... .... .. .. ..............
Dlbenzofuren (UC/l) 10. tI/ 20. U/ 10. U/ 10. u/ 10. II/R
2,l,-Olnltrotoluene WC/l) 10. III 20. U/ 10. U/ 10. U/ 10. U/R
Olethylphthelete (UG/l) 10. tI/ 20. U/ 10. U/ 10. U/ 10. U/R
I,-Chlorophenyt-phenylether (111./l) 10, U/ 20. UI 10. UI 10. U/ 10. U/R
Fluorene (UC/l) 10. tI/ 20. U/ 10. U/ 10. U/ 10. II/R
I,'Nltroenlllne (UG/l) 50. tI/ 100. U/ 50. U/ 50. U/ 50. II/R
1,,6-0Inltro-2-methylphenol (IIG/l) 50. tI/ 100. 11/ 50. 11/ 50. U/ 50. U/R
N-nltrosodiphenylemlne (UG/l) 10. tI/ 20. U/ 10. U/ 10. U/ 10. U/R
I,-Bromophenyl-phenylether (UG/l) 10. tI/ 20. U/ 10. U/ 10. U/ 10. U/R
Hexechlorobenzene (UG/l) 10. tI/ 20. U/ 10. U/ 10. U/ 10. U/R
Pentechlorophenol (UG/l) 50. tI/ 100. U/ 50. U/ 50. 11/ 50. II/R
Phenanthrene (UG/l) 10. tI/ 20. U/ 10. U/ 10. U/ 10. U/R
Anthrecene (UG/l) 10. tI/ 20. U/ 10. U/ II; U/ 10. U/R
OI'n-butylphthAIRte (UG/l) 10. U/ 20. U/ 10. U/ 10. II/ 10. II/R
rluorenthene (IIG/l) 10. U/ 20. II/ 10. U/ 10. U/ 10. U/R
Pyrene (UG/l) 10. U/ 20. U/ 10. U/ 10. U/ 10. II/R
Butylbenzylphthelete (UG/l) 10. U/ 20. U/ 10. U/ 10. U/ 10. U/R
3,]'-0Ichlorobenzldine (UG/l) 20. tI/ '0. U/ 20. U/ 20. U/ 20. II/R
Benzo(e)enthrecene (UG/l) 10. tI/ 20. U/ 10. U/ 10. U/ 10. II/R
Chrysene (UG/l) 10. U/ 20. U/ 10. U/ 10. 11/ 10. U/R
bls(2-ethylhexyl)phthelete (UG/l) 10. U/ 20. U/ 10. III 10. UI 10. II/R
DI-n-oetyl Phthelete (UG/l) 10. tI/ 20. tI/ 10. 11/ 10. U/ 10. U/R
Benzo(b)fluorenthene (UG/l) 10. U/ 20. U/ 10. U/ 10. U/ 10. U/R
Benzo(k)fluorenthene (UG/l) 10. U/ 20. U/ 10. U/ 10. U/ 10. U/R
Benzo(e)pyrene (UG/l) 10. U/ 20. U/ 10. U/ 10. U/ 10. U/R
Indeno(I,2,3-cd)pyrene (UG/l) 10. lI/ 20. U/ 10. U/ 10. U/ 10. U/R
Olbenz(e,h)enthrecene (UG/l) 10. U/ 20. U/ 10. U/ 10. U/ 10. U/R
Benzo(g,h,i)perylene (UG/l) 10. U/ 20. U/ 10. U/ 10. U/ 10. U/R
Note: (1) Results are H'ported with qualifiers (lahorAtory Quallfier/Dete Velidlltlon QUill If I er) to the right of the value.
I ,e.:
I t,:
-------
SUMMARY OF TENTATIVELY IDENTIFIED C~POUNDS
woodstock Landfill RIIFS
woodstock, Illinois
2
Matrix: LEC
\IK.LLIIOZ-01
08/08/90
(TBNA) Tentatively-Identified Semi-Volatiles
C OfII)Ound (Un its)
Concentration
LQ/cVO
............-........-----...---...........
..-.-.-..........-----..........
Trimethylbenzene
Trimethylbenzene
Unknown (UG/L)
Unknown (UG/L)
(UG/L>
(UG/L>
1'.
8.
1'.
12.
JI
JI
JI
JI
(TVCA) Tentatively-Identified Volatiles
COII1!)Ound (Un its)
Concentration
LQ/DVO
-.-.....--.----....--..-.-..............---
--....--.------...-...----.----.
Benzene, trimethyl- (UG/L)
Benzene, trimethyl- (UG/L)
Unknown (Ue/L)
Benzene, methylpropyl- (Ue/L)
Benzene, ethyldimethyl- (UG/L)
Benzene, ethyldimethyl- (UG/L)
Benzene, tetramethyl- (UG/L)
Unknown (UG/L)
Benzene, tetramethyl- (UG/L)
Naphthalene (UG/L)
37.
17.
16.
9.
11.
11.
. 10.
".
6.
17.
JI
JI
JI
JI
JI
JI
J/
J/
J/
JI
\IK-LLII02-02
02/07/91
(TBNA) Tentatively-Identified Semi-Volatiles
C~ (Units)
Concentration
LQ/CVCI
-.......-....----.-------------...----.....
----------.-----------------.-.-
Unknown (Ue/L)
Trimethylbenzene (UG/L)
2(3H)-benzothiazolone (UG/L)
Butoxyethanol phosphate (UG/L)
2'.
32.
2'.
16.
J/JN
J/JN
J/JN
J/JN
1/
-------
SUMMARY OF TENTATIVELY IDENTIFIED COMPOUNOS
woodstock landfill RIIFS
I/oodStock, III inois
3
Matrix: lEC
WIC-uw02-92
02/07/91
(TBNA) Tentatively-Identified Semi-Volatiles
Compound (Units)
Concentration
lQ/DVQ
-----------.--------------------..---------
---...--------------...---------
Unknown (UG/l)
Trimethylbenzene (UG/l)
Trimethylbenzene (UG/l)
Unknown alkenyl benzene (UG/l)
2(3H)-benzothiazolone (UG/l)
Ethanol, 2-butoxy-, phosphate (UG/l)
2'.
IJ..
16-
16.
28.
28.
J/JN
J/JN
J/JN
J/JN
J/JN
J/JN
(TVOA) Tentatively-Identified Yolatiles
Compound (Units)
Concentration
lQ/DVQ
-----------.---------------------------.---
------------.-------------------
Propyl benzene (UG/l)
8.
J/JN
l./K-llW03-01
08/08/90
(TBNA) Tentatively-Identified Semi-Volatiles
Compound (Units)
Concentration
lQ/DW
------------------------------------------.
----.-.-----.-------------......
Benzamide, N,N-diethyl-3-methy (UG/l)
Hexadecanoic acid (UG/l)
Hexanedioic acid, mono(2-ethyl (UG/l)
16.
"-
8.
JI
J/
JI
l./K-llW03-02
02/08/91
(TVOA) Tentatively-Identified Volatiles
Comcound (Units)
Concentration
lQ/DYQ
---------------------------.-----------.-.-
.-.-----------.-----------------
Unknown (UG/l)
3.
JI
\JIC-lLWO'-01
08/08/90
(TBNA) Tentatively-Identified Semi-Yolatiles
Compound (Units)
Concentration
lQ/DVQ
--------.-----------------------.........--
....-...-....-..-.--.------.-..-
Hexanoic acid, 2-methyl- (UG/l)
16.
JI
(TVOA) Tentatively-Identified Volatiles
Compound (Un;:s)
Concentration
LQ/DVQ
..._.__._~_..__.._._-_......~_...._----._.-
--------------.---...--.-----..-
Unknown (UG/~)
8.
JI
-------
I ~.
, I ~
ANALYTICAL DATA REPORT 4
Uoodstock landfill RI/rS
Uoodstock, IIlInoi 5
HatriIC: lEC Type: SVOC
Parameter UK-llUOZ.02 02/07/91 UK-llUOZ-9Z OZ/07/91 UK-llUO]-OI 08/08/90 UK-llU04-01 08/08/90 UK-LLU05-01 08/08190
- -...... -......oo..oooo .....oo oooooo - ... .. .... .......... --.... -.OO."OO"OO"OO -..- -oo.......... - ---..-......oooo---....---......oo.... -"-""-""-"-"---"OO---"--- -.....---oo--------.............-.... --....---..---..-..-..----.oo..-
Dlbenrofuran (UG/l) 20. U/ 20. UI 10. UI 10. UI 10. II/
2,4-Dlnitrotoluene (UG/l) ZOo UI 20. U/ 10. UI 10. UI 10. UI
Dlethylphthalate (UG/l) ZO. U/ 20. U/ 10. UI 10. UI 10. UI
4-Chlorophenyl-phenylether (UG/L) 20. UI 20. UI 10. UI 10. UI 10. III
Fluorene (UG/l) 20. UI 20. UI 10. U/ 10. UI 10. II/
4-NItroanlllne (UG/L) 100. UI 100. UI 50. U/ 50. UI 50. UI
4,6-Dlnltro-2-methylphenol (UG/l) 100. U/ 100. UI 50. U/ 50. U/ 50. UI
N.nltrosodlphenylamlne (UG/l) 20. U/ 20. UI 10. UI 10. UI 10. UI
4-Bromophenyl-phenylether (UG/l) 20. UI 20. U/ 10. UI 10. U/ 10. UI
HeKachiorobenrene (UG/l) 20. UI 20. U/ 10. UI 10. UI 10. ul
Pentachlorophenol (UG/l) 100. UI 100. U/ ]. JI 50. UI 50. II/
Phenanthrene (UG/l) 20. UI 20. UI 10. UI 10. U/ 10. UI
Anthracene (UG/l) 20. UI 20. U/ 10. UI 10. UI 10. U/
DI-n-butylphthalate (UG/l) 20. U/ 20. U/ 10. UI 10. UI 10. UI
rluoranthene (UG/l) 20. U/ 20. U/ 10. UI 10. UI 10. U/
Pyrene (UG/l) 20. UI 20. UI 10. UI 10. UI 10. UI
Buty1benrylphthalate (UG/l) 20. UI 20. U/ 10. UI 10. UI 10. UI
3,3'-Olehlorobenrldine (UG/l) 40. U/ 40. U/ 20. U/ 20. U/ ZOo III
Benlo(a)anthracene (UG/l) 20. U/ 20. U/ 10. UI 10. UI 10. III
Chrysene (UG/l) 20. UI 20. U/ 10. UI 10. UI 10. U/
bls(2'ethylhexyl)phthalate (UG/l) 20. UI 20. U/ 10. UI 10. UI 10. U/
Ol'n-oetyl Phthalate (UG/l) 20. U/ 20. U/ 10. UI 10. U/ 10. u/
Benlo(b)fluoranthene (UG/l) 20. UI 20. U/ 10. UI 10. UI 10. UI
Benlo(k)fluoranthene (UG/l) 20. III 20. U/ 10. UI 10. U/ 10. U/
Benlo(a)pyrene (UG/l) 20. UI 20. U/ 10. U/ 10. UI 10. u/
Indeno(I,2,]'ed)pyrene (UG/L) 20. U/ 20. U/ 10. U/ 10. UI 10. U/
Dlbenl(a,h)anthracene (UG/l) 20. UI 20. U/ 10. U/ 10. UI 10. UI
Benlo(g,h,l)perylene (UG/l) 20. U/ 20. u/ 10. U/ 10. U/ 10. U/
Note: (1) Results are reported with qualifiers (laboratory Qualifier/Data Validation Qualifier) to the right of the value.
-------
SUM~ARY OF TENTATIVELY IDENTIFIED COMPOUNDS
~oodstock Landfill RIIFS
~oodstock, Illinois
Matrix: LEC
Generated oy: CA~
Date Issued: i0-MAY-;i
\JI('Ulo'Oi-0i
05/08/90
(TBNA) Tentatively-Identified Semi-Volatiles
Compound (Units)
Concentration
LQ/OVQ
--..------.------...---....-.......-.......
..........--.----.-.---.-.----..
/,-(Tetramethylbutyl)phenol (Ue/L)
10.
JI
(TVOA) Tentatively-Identified Volatiles
Compound (Units)
Concentration
LQ/OVQ
-.----.---....----..--.....-.-.-...........
.......-..--------------....----
Benzene, trimethyl- (Ue/L)
Dichlorobenzene (Ue/L)
Benzene, trimethyl- (Ue/l)
1H-indene, dihydro- (Ue/L)
Ethyldimethylbenzene (Ue/l)
Ethyldimethylbenzene (Ue/l)
Benzene, tetramethyl- (Ue/L)
Ethyldimethylbenzene (Ue/l)
Ethyldimethylbenzene+unknown
(Ue/l)
9.
3-
3.
7.
3.
6.
3.
6.
8.
JI
JI
JI
JI
JI
JI
JI
JI
JI
\J(-LLW01-0Z
OZlOS/91
(TVOA) Tentatively-Identified Volatiles
Compound (Units)
Concentrlti on
lQ/OVCI
------.-.--.---........-.-.-------------.-.
--------------------------..----
Benzene, propyl- (Ue/l)
4.
JI
IJ('LLIJO'-9i
08/05/90
(TVCA) Tentatively-Identified Volatiles
Compound (Units)
Concentration
LQ/OVCI
.-.----..--....-..------.-.--.-..........-.
---...-...---.-.-.---.-.-.----.-
Benzene, trieethyl- (UG/l)
Benzene, propenyl- (UG/l)
Benzene, ethyldimethyl- (Ue/L)
Benzene, tetramethyl- (Ue/L)
Unknown suost. benzene (UC/L)
9.
7.
6.
6.
9.
JI
J/
J/
JI
J/
-
"
-------
SUMMARY OF TENTATIVELY IDENTIFIED COMPOUNDS
~oodstock Landfill RI/FS
~oodstock, Illinois
"
Matl"i)l: LEC
\,
\JK-LL~O"-02
02/08/91
(TVOA) Tentatively-Identified volatiles
COII'OOUnd (Uni ts)
Concentration
LQIOVQ
............-...................-.....--...
............................-..-
Ethane, 1 ,1' -_-,)'I)is' (UG/L)
Unknown (UG/L)
6.
6.
JI
JI
\JK'LL~05-01
08/08/90
(TBNA) Tentatively'Identified Semi-Volatiles
C 0II'00Und (Un its)
Concentration
LQIOVQ
..---...--.......----......----.-.------...
-......-.--.-...-.......-.-.....
Hexanoic acid (DOT) (UG/L)
Unknown (UG/L)
Unknown (UG/L)
Trimethylbenzene (UG/L)
Benzamide, N,W-diethyl-3-methy (UG/l)
Phenol, bis(dimethylethyl)-met (UG/l)
Unknown (UG/l)
1'.
1'.
16.
8.
8-
48.
8.
JI
JI
J/
JI
JI
JI
JI
(TVOA) Tentatively-Identified Volatiles
C~und (Units)
Concentration
LQ/DVQ
.-.-..--...---------.-..........-......-...
-.....-...........--.-..-.-.-.-.
Benzene, trimethyl- (UG/L)
Benzene, dichlaro' (UG/L)
Unknown subst. benzene (UG/l)
Unknown (UG/L)
1'.
,.
10.
6.
JI
JI
JI
JI
(/
.. -..
-------
"
LANDFILL GAS
-------
,- ,
Matrix: GAS Type: GSVOC
Generated by: CAU
Dote Issued: 10-HAY-91
Parameter
ANALYTICAL DATA REPORT
Uoodstock landfill RI/FS
Uoodstock, Illinois
---.......-...................
UK.GASfBOI-01 11/07/90
..-------------.-.-...--
UK-GASlU03-01 11/07/90
.......-...-.-.------.--
Freon 12 (PPB(V/V» Z.
Chloromethane (PPB(V/V» 2.5
Freon 114 (PPB(V/V» 2.
Vinyl chloride (PPB(V/V» 2.5
Bromomethane (PPB(V/V» - 3.
Chloroethane (PPB(V/V» 5.
Freon 11 (PPB(V/V» 1.
cis-I,2-0ichloroethene (PPB(V/V» 2.
Carbon disulfide (PPB(V/V» 10.
Freon 113 (PPB(V/V» 2.
Acetone (PPB(V/V» 10.
Methylene chloride (PPB(V/V» 4.
trans.I,Z-Oichloroethene (PPB(V/V» 4.
1,1-0ichloroeth8ne (PPB(V/V» 2.5
Vinyl 8cetate (PPB(V/V» 2_5
1,1-0Ichloroethene (PPB(V/V» 2.
2-Butanone (PPB(V/V» 3.
Chloroform (PPB(V/V» 2.
1,1,I-Trlchloroethane (PPB(V/V» 2.
Carbon tetrachloride (PPB(V/V» 2.
Benrene (PPB(V/V» 3.
1,2-0Ichloroeth8ne (PPB(V/V» 2.
Trlchloroethene (PP8(V/V» 2.5
1,Z-otchloropropane (PPB(V/V» 8.
Bromodichlorometh.ne (PPB(V/V» 2.
cls-I,3-0Ichloropropene (PP8(V/V» 3.
4'Methyl'2-pent8none (PPB(V/V» 3.
Toluene epPBeV/V») 3.
trons-I,3-0Ichloropropene (PPB(V/V» 3.
1,1,2-Trichloroethane (PPB(V/V» 3.
Tetrachloroethane (PPB(V/V» 3.
2-Hexanone (PPB(V/V» 5.
Oibromochloromethane (PPB(V/V» 3.
1,2'0ibromoethone (PPB(V/V» 2.
Chlorobenzene (PPB(V/V» 2.5
Ethylbenzene (PPO(V/V» 2_5
Xylenes (total) (PPB(V/V» 5.
Note: (1) Resul ts /Ire reported with qual ifiers
U/ 4. U/ 10.
U/ 5. U/ 13.
U/ 4. U/ 78.
U/ 5. U/ 13.
U/ 6. U/ 15.
U/ 10. U/ 470.
U/ 2. U/ 10.
U/ 4. U/ 20.
U/ 20. U/ 50.
U/ 4. U/ 10.
U/ 20. U/ 50.
U/ 8. U/ 20.
U/ 8. U/ 20.
UI 5- U/ 13.
U/ 5. U/ 13.
U/ 4. U/ 10.
U/ 6. U/ 15.
U/ 4. U/ 10.
U/ 4. UI 10.
U/ 4. U/ 10.
U/ 6. U/ 220.
U/ 4. U/ 10.
U/ 5. U/ 13.
U/ - 16. U/ 40.
U/ 4. U/ 10.
U/ 6. U/ 15.
U/ 6. U/ 15.
U/ 6. U/ 130.
U/ 6. U/ 15.
U/ 6. U/ 15.
U/ 6. U/ 15.
U/ 10. U/ 25.
U/ 6. U/ 15.
II/ 4- UI 10.
II/ 5. UI 120.
II/ 20. / 310.
U/ 20. / 440.
(labor.tory aual i fier/Data Vol idat Ion Quail tier)
UK-GASlU04-01 11/07/90
------------------------
U/
U/
/
U/
U/
/
U/
U/
U/
U/
U/
U/
U/
U/
U/
U/
U/
U/
U/
UI
/
UI
U/
UI
UI
U/
U/
1
U/
U/
U/
U/
U/
UI
/
1
/
to the right of
UK-GASlU04-91 11/07/90
-- -. ---- ..... ---.......-.. -----
10.
11.
48.
11.
15.
290.
10.
20.
50.
10.
50.
20.
20.
11.
13-
10.
15.
10.
10.
10.
120.
10.
13.
40.
10.
JS.
15.
65.
15.
15.
15.
25.
15.
10.
12.
190.
290.
the velue.
U/
U/
/
U/
U/
/
U/
U/
U/
U/
U/
U/
U/
U/
II/
II/
U/
U/
U/
U/
/
U/
U/
U/
U/
U/
U/
/
U/
II/
U/
U/
U/
UI
/
/
1
-------
ANALYTICAL DATA REPORT
Uoodstock Lendflll RI/FS
Uoodstock, Illinois
2
Hetrlx: GAS Type: GSVOC
Peremeter
UK-GASFBOI-01 11/07/90
UK-GASlU03-01 11/07/90
WK-GASLUO'-OI 11/07/90
UK-GASlUO'-91 11/07190
.....--.----..----------------
...... --- ---......... --- ..-.--..........
...-.---.-------...-.....-.
.------........ --.... .w..... -..........
-..-. ----.........-.............................
Styrene (PPB(V/V» 7. U/ 14. U/ 35. U/ 35. U/
Bromoform (prR(V/V» 2. U/ ,. U/ 10. U/ 10. U/
1,I,Z,Z-Tetrachloroethane (PPB(V/V» 4. U/ 8. U/ ZOo UI ZOo U/
Benzyl chloride (PPB(V/V» 2. U/ 4. U/ 10. U/ 10. U/
'.Ethyl toluene (PPB(V/V» 4. U/ 8. U/ 160. / 100- /
1,3,5-Trlmethylbenzene (PPB(V/V» Z.5 U/ 5. U/ 70. / 52. 1
1.2,4.Trlmethylbenzene (PPB(V/V» 3. U/ 25. 1 320. / 200. /
1.3.0Ichlorobenzene (PPB(V/V» 3. U/ 6. U/ 15. U/ 15. UI
I,4.0Ichlorobenzene (PPB(V/V» ,. U/ II. U/ 20. U/ 20. UI
I,2.Dlchlorobenzene (PPB(V/V» 5. UI '0. U/ 25. U/ 25. U/
I,2,4.Trichlorobenzene (PPB(V/V» 7. U/ 14. U/ 35. UI 35. U/
Hex8chlorobutediene (PPB(V/V» 5. U/ '0. U/ 25. U/ 25. U/
Note: (1) Re!:ults are reported ~ith qualifier!: (laboratory QUAlifier/Dota Validation Qualifier) to the right of the value.
I, "
------- |