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oooco
NATIONAL PRESTO INDUSTRIES, INC. SITE
EAU CLAIRE, WISCONSIN
LAGOON NO. 1
ENGINEERING EVALUATION/COST ANALYSIS
PROJECT #497-16.1
JULY 1997
Office Location: Office Contact:
EDER ASSOCIATES Nora M. Brew
480 Forest Avenue (516) 671 -8440
Locust Valley, New York 11560
Offices in New York, Wisconsin, Michigan, Georgia, Florida, New Jersey and Massachusetts
LLV5980.RPT 071697
eder associatesenvironmental scientists, and engineers
VIA FEDEX
July 16, 1997File #497-16.1
OFFICES:Locust Valley. .MYMadison. WlAnn Arbor. MlAugusta, GAJacksonville. FLTrenton. NJTampa, FLStoneham. MA
Mr. Michael BellotRemedial Project ManagerWaste Management DivisionUnited States Environmental Protection Agency - Region V77 West Jackson Boulevard - HSR6JChicago, Illinois 60604-3590
Re: National Presto Industries, Inc. SiteEau Claire, WisconsinLagoon No. 1 Engineering Evaluation/Cost Analysis
Dear Mr. Bellot:
Four copies of the Lagoon No. 1 Engineering Evaluation/Cost Analysis report (EE/CA) are enclosedfor your review, approval, and distribution to the information repositories. This report and thelaboratory data validation summary (submitted under separate cover) have been revised inaccordance with the USEPA and WDNR comments provided in your July 3, 1997 letter.
We are available to discuss the EE/CA at your convenience. Please call me (516-739-2094) orDennis Kugle in our Madison office (608-836-1500) if you have any questions.
Very truly yours,
EDER ASSOCIATES
Nora M. BrewSenior Engineer
NMB/llvcc: G. Mickelson
S.Thon0. PatelS. BauerR. NaumanD. Kugie
LLV59BO RPT
480 FOREST AVE., P 0. BOX 707, LOCUST VALLEY, NEW YORK 11560-0707 - (516) 671-8440 - FAX (516) 671-3349
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CONTENTS
Page
EXECUTIVE SUMMARY . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ES-1
1.0 INTRODUCTION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1
2.0 SITE CHARACTERIZATION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 22.1 Site Description and Background . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 22.2 Previous Remedial Actions . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 32.3 Lagoon No. 1 Waste Forge Compound Removal Action . . . . . . . . . . . . . . . . . . . 32.4 Lagoon No. 1 Vadose Zone Characterization . . . . . . . . . . . . . . . . . . . . . . . . . . . . 72.5 Risk Evaluation . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 13
3.0 IDENTIFICATION OF REMEDIAL OBJECTIVES . . . . . . . . . . . . . . . . . . . . . . . . . . . 143.1 Vadose Zone . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 143.2 Stockpiled Low BTU W a s t e / S o i l . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 143.3 ARARs . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 15
4.0 IDENTIFICATION AND ANALYSIS OF REMEDIAL ALTERNATIVES . . . . . . . . 164.1 Vadose Zone . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 17
4.1.1 Alternative V-l - No Further Action . . . . . . . . . . . . . . . . . . . . . . . . . . . . 174.1.2 Alternative V-2 - Soil Vapor Extraction . . . . . . . . . . . . . . . . . . . . . . . . . 194.1.3 Alternative V-3 - Composting in Biopiles . . . . . . . . . . . . . . . . . . . . . . . . 224.1.4 Alternative V-4 - Off-site Landfilling . . . . . . . . . . . . . . . . . . . . . . . . . . . 25
4.2 Stockpiled Waste/Soil . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 274.2.1 Alternative S-l - Consolidate Under MRDS Cap . . . . . . . . . . . . . . . . . . 274.2.2 Alternative S-2 - Soil Vapor Extraction . . . . . . . . . . . . . . . . . . . . . . . . . . 294.2.3 Alternative S-3 - Use as Supplemental Cement Kiln Fuel . . . . . . . . . . . 304.2.4 Alternative S-4 - Off-site Landfilling . . . . . . . . . . . . . . . . . . . . . . . . . . . 31
5.0 COMPARATIVE ANALYSIS OF REMEDIAL ALTERNATIVES . . . . . . . . . . . . . . . 335.1 Vadose Zone . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 335.2 Stockpiled Low BTU W a s t e / S o i l . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 37
6.0 RECOMMENDED REMEDIAL ALTERNATIVE . . . . . . . . . . . . . . . . . . . . . . . . . . . . 40
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TABLES
No. Description1 Summary of VOCs Detected in Soil - 19952 Summary of Soil Gas PGC Results - 19953 Summary of VOCs Detected in Soil -19964 Summary of Headspace PGC Results -19965 Summary of VOCs Detected in Groundwater - 1995/19966 Summary of SVOCs Detected in Soil - 19957 Summary of SVOCs Detected in Soil -19968 Summary of PCBs Detected in Soil - 19959 Summary of PCBs Detected in Soil - 1996
10 Summary of Metals Detected in Soil - 199511 Summary of Metals Detected in Soil - 199612 Preliminary Capital Cost Estimate, Alternative V-l - No Further Action13 Preliminary Capital Cost Estimate, Alternative V-2 - Soil Vapor Extraction14 Preliminary Capital Cost Estimate, Alternative V-3 - Composting in Biopiles15 Preliminary Capital Cost Estimate, Alternative V-4 - Off-site Landfilling16 Preliminary Capital Cost Estimate, Alternative S-l - Consolidate Under MRDS Cap17 Preliminary Capital Cost Estimate, Alternative S-4 - Off-site Landfilling
FIGURES
No. Description1 Site Plan2 Lagoon No. 1 Boring Locations3 Cross Section A-A'4 Vertical Profile of TCA Concentrations5 Vertical Profile of TCE Concentrations6 Vertical Profile of PCE Concentrations
APPENDICES
APPENDIX A—BORING LOGS AND BOREHOLE ABANDONMENT FORMSAPPENDIX B—APPLICABLE OR RELEVANT AND APPROPRIATE REQUIREMENTSAPPENDIX C—IRA GROUNDWATER REMEDIATION SYSTEM TIME FRAME ESTIMATES
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EXECUTIVE SUMMARY
This report is intended to satisfy the Engineering Evaluation/Cost Analysis (EE/CA) requirements
for Lagoon No. 1 at the National Presto Industries, Inc. (NPI) site, Eau Claire, Wisconsin, as
specified in the October 14, 1993 Administrative Order by Consent and the October 1994
Modification to this Order, which includes the "Amendment to Lagoon No. 1 Removal Action Work
Plan" (Eder Associates, October 1994). The goal of the EE/CA is to summarize the remedial
objectives related to residual contaminants remaining at the Lagoon No. 1 area and in the low BTU
value (<5,000 3TU/lb) waste/soil removed from Lagoon No. 1 (temporarily stockpiled near the
Melby Road Disposal Site [MRDS]). This EE/CA analyzes and compares the various alternatives
that may be used to satisfy these objectives.
Pursuant to the October 14,1993 Administrative Order by Consent, approximately 1,100,000 gallons
of pumpable waste forge compound (with heating values >5,000 BTU/lb) were removed from
Lagoon No. 1, blended with solvents, and burned as supplemental fuel at CERCLA-approved cement
kilns between October 1993 and September 1994. The October 1994 Modification to the Consent
Order addressed removing waste forge compound solids with heating values >5,000 BTU/lb from
Lagoon No. 1 and the East Disposal Site trench for use as a supplemental fuel at CERCLA-approved
cement kilns. The Modification also covered characterizing the vadose zone beneath Lagoon No.
1 and the East Disposal Site trench, evaluating remedial options, and remediating the vadose zone
at these areas, if necessary.
Approximately 5,000 cubic yards of waste forge compound solids (>5,000 BTU/lb) were removed
from the lagoon, packaged, transported to cement kilns and burned as supplemental fuel. After the
waste forge compound solids removal action was completed, a significant volume of waste/soil
mixture with BTU values less than 5,000 BTU/lb remained in Lagoon No. 1. USEPA suggested that
this material be removed from the lagoon and temporarily stockpiled near the MRDS, where it could
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eventually be consolidated with other waste materials from the East Disposal Site and Drainage
Ditch 3 and capped. Approximately 9,800 cubic yards of residual waste mixed with soil was
removed from Lagoon No. 1 in July - September 1996 and stockpiled near the MRDS. This EE/CA
is the administrative mechanism for evaluating options and making decisions regarding response
actions for this low BTU value waste/soil. USEPA's May 1996 Record of Decision (ROD) covers
remediation of the MRDS, East Disposal Site, Drainage Ditch 3, Dry Wells 2 and 5, and
groundwater in Plumes 1-2, 3, 4 and 5.
A well-defined waste forge compound trench was not found at the East Disposal Site and the
removal effort at this area was discontinued. The East Disposal Site vadose zone will be
characterized under the remedy described in the May 1996 ROD.
Soil samples were collected in August 1995 and September 1996 in accord with USEPA-approved
sampling plans. The samples were analyzed for TCL VOCs, SVOCs, PCBs and metals to
characterize the vadose zone beneath Lagoon No. 1. Soil gas and headspace screening analyses of
TCA, TCE and PCE were also performed to evaluate vapor phase VOC concentrations beneath the
lagoon. Although the sampling procedures were designed to minimize VOC loss prior to laboratory
analysis, the laboratory reported few detectable concentrations of VOCs in the soil samples. The
PGC soil gas and headspace screening analyses were more sensitive and detected VOCs more
frequently than the laboratory analyses.
The SVOCs detected in the soil samples are consistent with the asphaltic material which comprised
one-third of the forge compound, and indicate that small amounts of waste forge compound remain
mixed with soil near the surface at some locations in Lagoon No. 1. The concentrations of PCBs
and metals detected in the soil samples are not of concern.
The characterization results indicate that residual VOCs in the vadose zone beneath the lagoon
would act as a very low level source of contaminants to groundwater as precipitation and runoff
infiltrate through the subsurface, until the remaining VOCs are washed out.
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The following alternatives were evaluated to remediate residual VOCs in the vadose zone beneath
Lagoon No. 1 and to dispose of the stockpiled low BTU waste/soil:
Vadose Zone Alternatives
• Alternative V-l - No Further Action
• Alternative V-2 - Soil Vapor Extraction
• Alternative V-3 - Composting in Biopiles
• Alternative V-4 - Off-site Landfilling
Stockpiled Waste/Soil Alternatives
Alternative S-l - Consolidate Under MRDS Cap
• Alternative S-2 - Soil Vapor Extraction
• Alternative S-3 - Use as Supplemental Cement Kiln Fuel
• Alternative S-4 - Off-site Landfilling
These alternatives were evaluated and compared based on effectiveness, implementability and cost.
Based on this evaluation, NPI and Eder recommend installing ar CWT7 c"stem to remove residual
vapor phase VOCs from the vadose zone beneath Lagoon No. 1, and consolidating the stockpiled
low BTU waste/soil for capping at the MRDS.
NPI and Eder are prepared to quickly design and install the Lagoon No. 1 SVE system in 1997, upon
approval from USEPA and WDNR. The stockpiled waste/soil would be removed and consolidated
at the MRDS in step with installation of the MRDS cap planned for 1998.
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1.0 INTRODUCTION
This report is intended to satisfy the Engineering Evaluation/Cost Analysis (EE/CA) requirements
for Lagoon No. 1 at the National Presto Industries, Inc. (NPI) site, Eau Claire, Wisconsin, as
specified in the October 14, 1993 Administrative Order by Consent and the October 1994
Modification to this Order, which includes the "Amendment to Lagoon No. 1 Removal Action Work
Plan" (Eder Associates, October 1994). The goal of the EE/CA is to summarize the remedial
objectives related to residual contaminants remaining at the Lagoon No. 1 area and in the low BTU
value (<5,000 BTU/lb) waste/soil removed from Lagoon No. 1 (temporarily stockpiled near the
MRDS). This EE/CA analyzes and compares the various alternatives that may be used to satisfy
these objectives. This EE/CA report is consistent with USEPA's Guidance on Conducting Non-
Time-Critical Removal Actions Under CERCLA (EPA/540-R-93-057, August 1993).
Details on the waste forge compound removal action conducted at Lagoon No. 1 and relevant
historical and site characterization information are presented in Section 2.0. Remedial objectives
related to residual contaminants remaining at the Lagoon No. 1 area and in the stockpiled low BTU
value waste/soil are developed in Section 3.0. Alternatives to achieve the remedial objectives for
these materials are evaluated separately in Section 4.0 and compared in Section 5.0. The
recommended alternative is identified in Section 6.0.
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2,0 STTF CHARACTERIZATION
2.1 Site Description and Background
The NPI site Remedial Investigation (RI) report (Eder, August 1994) and Feasibility Study (FS)
report (Eder, September 1995) present detailed information on site history, waste disposal practices,
and the nature and extent of contamination at the NPI site and in groundwater at and around the site.
The FS did not address remediation of Lagoon No. 1, since this area was addressed separately under
the October 1993 Consent Order and the October 1994 Modification. Figure 1 is a site plan of
Lagoon No. 1. The FS developed remedial alternatives for the Melby Road Disposal Site (MRDS),
the East Disposal Site, Drainage Ditch 3, Dry Wells 2 and 5, and off-site groundwater in Plumes 1-2,
3,4 and 5. The May 1996 Record of Decision (ROD) for the NPI site selected the following remedy
for these areas of concern:
• In-situ soil vapor extraction (SVE) at the MRDS
• Multi-layer capping at the MRDS
• Removing waste materials from the East Disposal Site and Drainage Ditch 3 and
consolidating them at the MRDS for capping
• Removing contaminated soil and sediment from Dry Wells 2 and 5 for off-site
disposal
• Long-term groundwater, surface water, and SVE system monitoring
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2.2 Previous Remedial Actions
Several remedial actions have been taken to address groundwater contamination and areas of concern
at the NPI site as discussed below.
NPI provided bottled water to portions of the Town of Hallie and the City of Eau Claire in the
affected area north and east of the NPI site pursuant to an April 25,1989 Unilateral Order issued by
USEPA. A permanent replacement drinking water supply was extended to the affected area as a
result of a March 8,1991 Unilateral Order. By March 1992, all homes and businesses in the affected
area were connected to a permanent replacement drinking water supply. Under existing private well
ordinances, no private wells in the affected area are used to obtain potable water. This was
confirmed by a private well survey completed in 1995.
The Eau Claire Municipal Well Field (ECMWF) is located approximately 2.5 miles west of the NPI
site. VOCs were detected in municipal wells at concentrations above Wisconsin groundwater
standards in 1984 -1985. An air stripper was installed at the ECMWF in 1987, and a March 1988
ROD selected continued operation of the air stripper as the final remedy for the ECMWF site.
In September 1991, USEPA issued an interim action ROD that addressed groundwater at the NPI
site. The interim action was designed to prevent the off-site migration of contaminated groundwaterfrom the MRDS and the southwestern portion of the NPI site. Groundwater extracted under the
interim action is treated by cascade aeration to reduce VOC concentrations prior to discharge to the
Chippewa River via the storm sewer system. The interim action extraction and treatment system
began operating in March 1994. Groundwater monitoring indicates that the interim action objectives
are being met.
2.3 Lagoon No. 1 Waste Forge Compound Removal Action
Lagoon No. 1 was used as part of the wastewatei disposal system at the NPI site. Between 1966 and
1980, liquid waste, solids, cooling water and process wastewater were discharged to Lagoon No. 1,
which was used as a settling pond. The waste forge compound settled to the bottom of the lagoon
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and oils floated to the top, leaving a layer of water between the oil and the waste forge compound.
Water was then pumped from Lagoon No. 1 into seepage Lagoon No. 2. The discharge lines from
the manufacturing plant were permanently sealed off from Lagoon No. 1 in 1985.
Treatability studies conducted on the Lagoon No. 1 waste forge compound indicated that this
material had a heating value of about 10,000 BTU/lb, which is above the 5,000 BTU/lb threshold
required for supplemental waste fuels. In 1993, NPI solicited a proposal from Waste Research and
Reclamation Co., Inc. (WRR) of Eau Claire to remove the waste forge compound from the lagoon
by pumping it into tankers, blending it with waste solvents to reduce its viscosity, and burning the
mixture as a liquid supplemental fuel in an off-site cement kiln.
In July 1993, a pilot study was conducted in accordance with a USEPA-approved work plan to
evaluate the feasibility of the WRR proposal. The pilot study documented that it was feasible to
remove and blend the waste forge compound from Lagoon No. 1 for use as a supplemental fuel in
a cement kiln. The pilot study results are summarized in the "Lagoon 1 Removal Action Work Plan"
(Eder, October 1993). NPI recommended full scale implementation of the Lagoon No. 1 waste forge
compound removal and fuel blending alternative based on the success of the pilot study. USEPA
issued an Administrative Order by Consent to NPI effective October 14, 1993 for the Lagoon No.
1 waste forge compound removal action.
The removal action began in October 1993 with the removal of approximately 14,000 gallons of
floating oil from the northeastern corner of Lagoon No. 1. The oil was disposed of through the
cement kiln fuels program. The standing water was left in the lagoon to allow the use of a barge
mounted pump and auger to remove the waste forge compound. Approximately 1,100,000 gallons
of pumpable waste forge compound were removed from Lagoon No. 1, blended with solvents, and
burned as supplemental fuel at CERCLA-approved cement kilns between October 1993 and
September 1994. This removal action was completed for approximately $2,500,000, which included
the removal, blending, transportation, and burning of the pumpable waste forge compound;
equipment and supplies; equipment decontamination; engineering services; and project
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administration. The work is summarized in the "Lagoon No. 1 Waste Forge Compound Removal
Action Interim Status Report" (Eder, December 1994).
After the waste forge compound removal action was completed, Lagoon No. 1 contained standing
water and residual waste forge compound mixed with soil at the bottom and sides of the lagoon.
WRR evaluated the feasibility of using waste solids with high BTU values from the lagoon and the
East Disposal Site as supplemental cement kiln fuels. WRR developed a proposal to remove residual
waste forge compound solids from the bottom and side walls of Lagoon No. 1 and buried waste
forge compound from the trench at the East Disposal Site, and to use these materials as supplemental
fuels at a cement kiln.
In October 1994, USEPA issued a Modification to the October 14, 1993 Consent Order which
included the "Amendment to Lagoon No.l Removal Action Work Plan" (Eder, October 1994) and
addressed the following tasks:
• Removing waste forge compound solids with heating values >5,000 BTU/lb from
Lagoon No. 1 and the East Disposal Site trench
• Processing the waste forge compound solids to achieve a homogeneous material and
packaging the materials in plastic buckets
• Transporting the packaged materials off-site for use as a supplemental fuel at
CERCLA-approved cement kilns
• Characterizing the vadose zone beneath Lagoon No. 1 after removing overlying
waste forge compound solids, evaluating remedial options, and remediating the
vadose zone at this area, if necessary
• Characterizing the vadose zone beneath the East Disposal Site trench after removing
buried waste forge compound solids
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Waste forge compound solids removal activity began in the southern lobe of Lagoon No. 1 in
November 1994. Standing water was removed from the lagoon in step with the removal activity.
The water was pumped into settling tanks for oil/solids separation and then analyzed prior to
discharge to the City of Eau Claire sanitary sewer system. The waste forge compound solids were
removed from the lagoon using a backhoe. The extent of waste removal was determined based on
visual observations of the waste-native soil interface and BTU value. WRR packaged the waste in
plastic buckets for transportation to CERCLA-approved cement kilns for use as supplemental fuel.
WRR constructed an access road from the southern lobe of the lagoon through the main lobe to
facilitate movement of the backhoe and removal activities. WRR completed removing the burnable
waste forge compound solids (>5,000 BTU/lb) from Lagoon No. 1 in December 1995.
An extensive ambient air monitoring program conducted at the Lagoon No. 1 area during the waste
forge compound solids removal activity verified that emissions of VOCs, SVOCs and particulates
were minimal and did not pose a risk to on-site workers or area residents.
The approximate extent of the East Disposal Site trench was delineated based on the RI results.
WRR used a backhoe to excavate in this area, but did not find a well-defined waste forge compoundtrench. Small amounts of waste forge compound mixed with soil were found sporadically at this
area, and did not warrant removal for the cement kiln fuels program. The waste forge compound
removal effort at the East Disposal Site was discontinued in November 1995 with concurrence from
USEPA.
After the waste forge compound solids removal action was completed, a significant volume of
waste/soil mixture with BTU values less than 5,000 BTU/lb remained in Lagoon No. 1. USEPA
suggested that this material be removed from the lagoon and temporarily stockpiled near the MRDS,
where it could eventually be consolidated with other waste materials from the East Disposal Site and
Drainage Ditch 3 and capped. This EE/CA is the administrative mechanism for evaluating options
and making decisions regarding response actions for this low BTU value waste/soil. Removal of
the residual waste from the lagoon facilitated vadose zone characterization activities. Approximately
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9,800 cubic yards of residual waste mixed with soil was removed from Lagoon No. 1 in July -
September 1996 and stockpiled near the MRDS. This stockpiling activity was conducted in
accordance with Chapter NR 718, Wisconsin Administrative Code. USEPA inspected the lagoon
in September 1996 and determined that no additional removal of residual waste was required.
Approximately one hundred 55-gallon drums of low BTU value waste/soil accumulated during the
waste forge compound solids removal action are stored on the covered loading dock near Lagoon
No. 1. This material will be consolidated with the low BTU material stockpiled near the MRDS.
The alternatives evaluated in this EE/CA for stockpiled waste/soil include the material from these
drums, bringing the total volume of waste/soil to approximately 10,000 cubic yards.
The waste forge compound solids removal action was completed for approximately $4,000,000,
which included the removal, packaging, transportation, and burning of approximately 5,000 cubic
yards of waste forge compound solids (>5,000 BTU/lb); removal and stockpiling of approximately
9,800 cubic yards of residual waste forge compound solids (< 5,000 BTU/lb); equipment and
supplies; equipment decontamination; engineering services; and project administration.
2.4 Lagoon No. 1 Vadose Zone Characterization
The vadose zone beneath Lagoon No. 1 was characterized in August - September 1995 (southern
lobe) and September 1996 (western and northern lobes) in accordance with the October 1994 work
plan and sampling plan amendment letters approved by USEPA. The southern lobe was sampled
after the burnable waste forge compound solids were removed from this lobe. The western and
northern lobes were sampled after the burnable waste forge compound solids and residual waste
removal was completed.
No vadose zone sampling was conducted at the East Disposal Site since the waste removal action
was discontinued at this location. The East Disposal Site will be characterized under remedy
described in the May 1996 ROD.
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The Lagoon No. 1 vadose zone sampling and characterization results are described below.
Sampling Activity - August/September 1995
Six soil borings (B-l through B-6) were drilled through the southern lobe of the lagoon and one
boring (B-7) was drilled just south of this lobe at the locations shown on Figure 2. The southern
lobe sampling was conducted from August 30 - September 1, 1995. These borings were drilled
using 7-inch O.D. hollow stem augers. Soil samples were collected at five-foot intervals and all of
the borings were drilled to bedrock. Soil samples were collected from borings B-l, B-2, B-3, B-4,
B-5 and B-7 in 24-inch x 2.5-inch diameter stainless steel liners placed inside split-spoon samplers.
The split-spoon samplers were decontaminated and rinsed with distilled water between each sample.
Immediately after retrieving the sampler from the boring, the stainless steel liner was capped on both
ends, sealed with Teflon tape and placed in a cooler on ice. Granular bentonite was used to
completely fill any headspace in the sample tube. The samples were shipped to the laboratory
(Quanterra Environmental Services, North Canton, Ohio) via overnight courier. These sampling
methods were used in an attempt to minimize VOC loss from the samples. The samples were not
exposed to air until just prior to analysis in the laboratory. The samples were analyzed for TCL
VOCs, SVOCs and PCBs, and TAL metals in accordance with ^^~ ^ctocol.
Groundwater was present above the bedrock in B-2. A groundwater sample was collected using a
disposable bailer inside the augers from this borehole. The groundwater sample was submitted to
the laboratory (Hazleton Environmental Services, Madison, Wisconsin) for analysis of TCL VOCs
in accordance with CLP protocol.
Boring B-6 was drilled to characterize the lithology of the unsaturated materials beneath Lagoon No.
I. No samples were collected from B-7 for laboratory analysis.
Soil cuttings were placed on plastic sheeting adjacent to each borehole and covered with plastic. The
boreholes were abandoned using granular bentonite. Copies of the boring logs and borehole
abandonment forms are included in Appendix A.
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Seven soil gas samples were collected on September 7, 1995, one foot north of each soil boring
location. The soil gas samples were taken from approximately five feet below grade. A 0.5-inch
diameter steel rod was driven to a depth of five feet and removed. A 0.25-inch stainless steel tube
was then placed in the hole. The steel rod and stainless steel tube were decontaminated betweeneach sample. Air (> one liter/minute) was purged from the stainless steel tube for at least three
minutes before collecting a sample. The soil gas samples were collected in aluminum vacuum
canisters and shipped to Eder's New York office via overnight courier for portable gas
chromatograph (PGC) analysis of TCA, TCE and PCE.
Sampling Activity - September 1996
USEPA inspected the Lagoon No. 1 and MRDS areas on September 3, 1996 to evaluate the low
BTU residual waste removal and stockpiling progress. Additional waste was removed from the
lagoon and two grab samples of stained soil (NPIL1SSA and NPIL1SSB) were collected on
September 4, 1996 for laboratory analysis of TCL VOCs, SVOCs, and PCBs, and TAL metals by
CLP protocol as requested by USEPA.
?- "nteen soil borings (B-8 through B-24) were drilled in the western and northern lobes of thelagoon at the locations shown on Figure 2. Sampling was conducted between September 16 and 24,
1996. The boring locations were approved by USEPA in the field before drilling began. Two
additional grab samples (G-l and G-2) of suspected waste forge compound material were collected
along the access road approximately 0.5 feet below grade as requested by USEPA. Borings B-8
through B-20 were drilled and samples were collected as described in the USEPA-approved
sampling plan amendments. Borings B-21 through B-24 were added at locations selected by USEPA
in order to visually characterize subsurface materials along and beneath the access road. No samples
were collected for analysis from these borings. These additional borings were advanced until there
was no visual evidence of staining in the split spoon samples. Dark stained soil was found in borings
B-21 to approximately 3 feet, B-22 to one foot, and B-23 and B-24 to 8 feet.
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The borings were drilled using 4.25-inch O.D. hollow stem augers. Soil samples were collectedfrom B-8 through B-20 at five-foot intervals from the surface to 10 feet, and at 10-foot intervals until
bedrock was reached. Soil samples were collected from these borings in four 6-inch x 2.5-inch
diameter stainless steel liners placed inside 24-inch split-spoon samplers. If two full liners could not
be recovered from a sampling interval, the split spoon was advanced another 24 inches with clean
liners. The split-spoon samplers were decontaminated and rinsed in distilled water between each
sample. Immediately after retrieving the sampler from the boring, the stainless steel liner was
capped on both ends, sealed with Teflon tape and placed in a cooler on ice. Granular bentonite was
used to completely fill any headspace in the sample tubes.
At least one full liner for each sample interval was shipped to the laboratory (Quanterra) via
overnight courier; another liner was sent to Eder's New York office for PGC headspace analysis to
develop a vertical profile of VOCs in the soil gas. The samples were not exposed to air until just
prior to analysis. The laboratory analyzed the samples for TCL VOCs, SVOCs and PCBs, and TAL
metals in accordance with CLP protocol. Samples collected from 20 feet to bedrock were analyzed
for SVOCs and PCBs only if these compounds were detected in the samples collected above 20 feet
in the respective borings. Headspace concentrations of TCA, TCr rtnH PCE were quantified using
the PGC.
Groundwater was present above the bedrock in B-8 and B-9. Groundwater samples were collected
from these boreholes using a clean bailer inside the augers. The groundwater samples were
submitted to the laboratory (Quanterra) for analysis of TCL VOCs in accordance with CLP protocol.
Soil cuttings were placed on plastic sheeting adjacent to each borehole and covered with plastic. The
boreholes were abandoned using granular bentonite. Copies of the boring logs and borehole
abandonment forms are included in Appendix A.
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Analytical Results
The laboratory analytical results were validated in accordance with USEPA data validation
guidelines. The complete data validation summary and tables have been forwarded under separate
cover. The validated data are summarized in the following tables. Only the detected compounds
are included in these tables for clarity.
Table 1 - Summary of VOCs Detected in Soil - 1995
Table 2 - Summary of Soil Gas PGC Results -1995
Table 3 - Summary of VOCs Detected in Soil - 1996Table 4 - Summary of Headspace PGC Results - 1996
Table 5 - Summary of VOCs Detected in Groundwater - 1995/1996
Table 6 - Summary of SVOCs Detected in Soil - 1995
Table 7 - Summary of SVOCs Detected in Soil - 1996
Table 8 - Summary of PCBs Detected in Soil -1995
Table 9 - Summary of PCBs Detected in Soil -1996
• Table 10 - Summary of Metals Detected in Soil -1995
• Table 11 - Summary of Metals Detected in Soil - 1996
The main contaminants of concern at the NPI site are TCA, TCE and PCE, the VOCs that
characterize groundwater contamination in the plumes downgradient of the site. The RI determined
that SVOCs, PCBs and metals (except for cadmium in Plume 1 -2 at the Lagoon No. 1 area) do not
impact groundwater quality, however the Lagoon No. 1 vadose zone sampling effort included these
compounds to fully characterize the subsurface materials.
VOCs - Although the sampling procedures were designed to minimize VOC loss prior to laboratory
analysis, the laboratory reported few detectable concentrations of VOCs in the soil samples collected
in 1995 and 1996. Most of the VOCs were detected in the near surface samples; none were detected
in samples from depths below 7 feet. The highest reported concentrations of the target VOCs are
780 ug/kg TCA, 26 ug/kg TCE, and 320 ug/kg PCE, all from boring B-9,1-1.5' sample. The 5.5-6'
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sample from this boring had significantly lower concentrations, and no VOCs were detected in
samples below 6 feet.
The PGC soil gas and headspace screening analyses were more sensitive and detected VOCs more
frequently than the laboratory analyses. There is no correlation between the laboratory and the PGC
data.
The 1995 shallow soil gas sampling results detected TCA (12,705 to 91,410 ppb), TCE (54 to 472
ppb) and PCE (59 to 484 ppb) at each boring location (TCA was not detected at B-7). The lowest
concentrations of TCA and PCE were found in B-7, just south of the lagoon. Based on these results,
the 1996 investigation included headspace sampling at depth to develop a vertical profile of VOC
vapor concentrations in the subsurface. TCA, TCE and/or PCE were detected in the sample
headspace from most of the samples collected from the surface to bedrock in borings B-8, B-9, B-10,
B-l 1, B-13, B-15A, B-16, B-17 and B-18B. The headspace VOC concentrations tend to decrease
with depth.
Figure 3 shows a cross section line through Lagcon No. 1. Figures 4, 5 and 6 show the vertical
profiles of TCA, TCE and PCE concentrations reported by the laboratory and the PGC for the
borings along this cross section. These data are representative of VOCs in the vadose zone beneath
the lagoon.
The groundwater samples collected from borings B-2, B-8 and B-9 contained several VOCs. TCE
(0.2 to 20 ug/I), TCA (20 to 41 ug/1) and 1,1-DCA (9 to 35 ug/1) were detected in all the samples.
Low levels of PCE (0.5 to 2 ug/1) and toluene (0.7 ug/1) were detected in the samples from B-2 and
B-8.
No VOCs were detected by the laboratory in grab samples NPIL1SSA and NPIL1SSB. TCA (20
to 61 ug/kg) was detected in grab samples G-1 and G-2; PCE (21 ug/kg) was also found in G-2.
These levels are at the low end of the range of VOC concentrations detected by the laboratory.
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SVOCs - SVOCs were detected in samples collected from the surface to a depth of 10 feet in borings
B-8, B-9, B-10, B-12A, B-13, B-16 and B-17, therefore the laboratory was directed to analyze the
held samples (from 20 feet to bedrock) from these borings. The largest number of SVOCs, including
phenanthrene (880 ug/kg), flouranthene (760 ug/kg), pyrene (1,200 ug/kg), and benzo(a)anthracene
(480 ug/kg) were detected in the surface sample from B-8 (0.5-11). The SVOCs detected in the soil
samples and grab samples are consistent with the asphaltic material which comprised one-third of
the forge compound, and indicate that small amounts of waste forge compound remain mixed with
soil near the surface at some locations in Lagoon No. 1.
PCBs - Aroclor-1254 was detected in soil from B-7 (surface sample, 99.8 ug/kg) and B-16 (11-11.5'
sample, 14 ug/kg). These concentrations are not of concern. No PCBs were detected in the grab
samples.
Metals - The concentrations of metals detected in the soil samples are consistent with background
concentrations determined during the RI.
2.5 Risk Evaluation
The results of USEPA's baseline risk assessment (Weston, 1992) for the NPI site are summarizedin the RI/FS. The baseline risk assessment represents pre-removal conditions at Lagoon No. 1 and
therefore overstates the current risks. The only pathways for exposure to residual contaminants at
Lagoon No. 1 are dermal absorption, inhalation and ingestion. The risks associated with these
exposures have been greatly reduced by the removal actions completed at this area. The most
concentrated mass of contaminants at the NPI site has been eliminated by the Lagoon No. 1 waste
forge compound and waste forge compound solids removal actions, essentially eliminating human
health risks. Small amounts of waste forge compound remain mixed with soil near the surface at
some locations in Lagoon No. 1, which may pose a risk if the lagoon is not backfilled or covered to
prevent direct contact. Residual VOCs in the vadose zone beneath the lagoon would act as a very
low level source of contaminants to groundwater as precipitation and runoff infiltrate through the
subsurface, until the remaining VOCs are washed out.
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3,0 IDENTTFirATTON OF REMEDIAL OBJECTIVES
3.1 Vadose Zone
The following are the remedial objectives for residual contamination in the vadose zone at the
Lagoon No. 1 area.
• Prevent direct contact with the small amount of waste forge compound mixed with
soil that remains in the lagoon to eliminate human health risks.
• Remove residual VOC vapors from the vadose zone to eliminate the low level source
of groundwater contamination.
• Reduce or minimize infiltration of precipitation through any contaminated materials
that remain in the lagoon.
• Continue to operate the interim remedial action (IRA) extraction system at the
southwestern portion of the NPI site to prevent off-site migration of VOCs in
groundwater until the Wisconsin PALs are achieved or concentrations are reduced
to the lowest possible levels (as agreed with USEPA and WDNR) below the MCLs
and Enforcement Standards in on-site groundwater at the Lagoon No. 1 area.
3.2 Stockpiled Low BTU Waste/Soil
The following are the remedial objectives for the low BTU value (<5,000 BTU/lb) waste/soil
removed from Lagoon No. 1 and temporarily stockpiled near the MRDS.
• Remove the stockpiled waste/soil from the temporary storage areas for final disposal.
• Prevent direct contact with the stockpiled waste/soil to eliminate human health risks.
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• Reduce or minimize infiltration of precipitation through the low BTU waste/soil.
3.3 ARARs
Applicable or relevant and appropriate requirements (ARARs) for the Lagoon No. 1 remedial
alternatives are summarized in Appendix B. The remedy selected for the vadose zone beneath the
lagoon and the low BTU waste/soil would be required to comply with ARARs.
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4tQ IDENTIFICATION AND ANALYSTS OF REMEDIAL ALTERNATIVES
This EE/CA addresses the following Lagoon No. 1 materials:
• Residual vapor phase VOCs in the vadose zone.
• Approximately 9,800 cubic yards of low BTU value (<5,000 BTU/lb) waste forge
compound material that is stockpiled near the MRDS and approximately 100 drums
of low BTU waste/soil stored on the loading dock near Lagoon No. 1.
• Small amounts of waste forge compound mixed with soil that remain at the bottom
of the lagoon, and waste forge compound material beneath the access road in the
western lobe of the lagoon.
The small amount of waste forge compound mixed with soil near the bottom of the lagoon poses a
minimal source of contaminants to groundwater, given the low c^.^.-^iions of VOCs detected in
the soil and headspace samples. This material would remain in the lagoon, since it is not feasibleto remove the minor amount of waste forge compound that remains mixed with large amounts of soil
at Lagoon No. 1. The potential for VOCs to diffuse from this residual material into soil vapor will
be considered when evaluating and designing remedial alternatives for the vadose zone beneath thelagoon.
The following remedial alternatives have been developed separately for the vadose zone and the
stockpiled low BTU waste/soil to achieve the objectives outlined in Section 3.0.
Vadose Zone Alternatives
Alternative V-l - No Further Action
• Alternative V-2 - Soil Vapor Extraction
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The IRA system would have to operate for an estimated ten years if the no action approach is taken.
Estimates of the IRA system operating time frame with and without source removal are presented
in Appendix C. The actual time frame would be determined based on groundwater monitoring
results. The annual O&M and monitoring cost associated with the IRA system at the southwestern
portion of the site is approximately $40,000.
WDNR's NR 720 regulations provide for the development of site-specific soil cleanup levels based
on groundwater protection. USEPA has indicated that contaminant transport modeling would be
required under this alternative to demonstrate that the residual concentrations of VOCs in the vadose
zone beneath Lagoon No. 1 would not cause the Wisconsin groundwater standards to be exceeded.
Contaminant transport modeling would involve selecting an appropriate model, agreeing on the
model set up and assumptions, calibrating the model, conducting a sensitivity analysis, and
interpreting the modeling results. Given the number of assumptions that would have to be made,
it is probable that the model results would not be conclusive. In the end, the calculated soil cleanup
standards may be less than the residual VOC levels, so action such as SVE may still have to be taken
to remove VOCs from the vadose zone.
Effectiveness - The no further action alternative would effectively eliminate human health risks
posed by direct contact with contaminants remaining at the Lagoon No. 1 area. This alternative
would rely on natural attenuation to comply with ARARs over the long term. Natural flushing
would wash residual vapor phase VOCs out of the vadose zone over time and into groundwater. The
IRA extraction system would continue operating for an estimated 10 years to prevent the off-site
migration of VOCs in groundwater at concentrations above the Wisconsin groundwater standards
and protect the environment. The actual time frame would be determined based on groundwater
monitoring results. Risks to workers during placement of backfill in the lagoon would be addressed
by a site-specific health and safety plan.
The no further action alternative does not include treatment and would rely on continued operation
of the IRA extraction system to prevent off-site migration of VOCs in groundwater. Natural
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attenuation would eliminate the residual source of groundwater contamination over the long term.
The IRA system would be operated and maintained until VOC concentrations in on-site groundwater
at the Lagoon No. 1 area are reduced to below the PALs or to the lowest possible levels below the
MCLs and Enforcement Standards.
Implementability - This alternative is technically feasible and could be readily implemented by NPI
or a local contractor using suitable on-site materials as backfill. Backfill material could also be
imported if needed. Materials would be sampled and characterized by a certified laboratory before
being used as backfill. The lagoon could be backfilled within approximately two months of USEPA
approval. No off-site treatment or disposal would be required under this alternative.
Contaminant transport modeling to develop MR 720 site-specific soil cleanup levels and support the
no action alternative would require many assumptions and it is probable that the modeling would
not conclusively demonstrate that the concentrations of residual vapor phase VOCs in the vadose
zone would not cause the groundwater standards to be exceeded.
No permits, easements or rights of way would be required to implement this alternative. There
would be no impacts on adjacent properties and no need for institutional controls.
Cost - The estimated cost of this alternative is $366,000, which includes $40,000 for contaminant
transport modeling per NR 720. The cost estimate is summarized in Table 12. No operation and
maintenance costs would be associated with this alternative.
4.1.2 Alternative V-2 - Soil Vapor Extraction
Under this alternative, an in-situ SVE system would be installed to remove residual VOC vapors
from the vadose zone beneath Lagoon No. 1. The lagoon would be backfilled once SVE operation
is completed and the SVE equipment is removed. USEPA has indicated that NR 720 site-specific
soil cleanup levels would not have to be developed if NPI decides to take action to remove
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subsurface VOC vapors (VOCs would be removed to non-detectable levels), making cleanup levels
a moot point since there would be no residual concentrations.
The SVE system should remove the residual vapor phase VOCs that act as a low level source of
groundwater contamination. VOCs would not continue to leach to groundwater once they are
removed. VOC concentrations in on-site groundwater should reach the PALs or be reduced to the
lowest possible levels in significantly less time than the no action alternative, so the IRA system
could be shut down more quickly. The IRA system at the southwestern portion of the NPI site
should operate for an estimated five years under the SVE alternative (source removed) versus ten
years for the no action alternative (source remains). Estimates of the IRA system operating time
frame with and without source removal are presented in Appendix C. The actual time frame would
be determined based on groundwater monitoring results.
The SVE system would be designed to capture soil vapor beneath the entire extent of Lagoon No.
1, since VOCs have been detected in soil vapor samples collected at different depths in nearly all of
the borings drilled in the lagoon. A conceptual SVE system design was developed based on the
results of the SVE pilot study conducted at the MRDS (summarized iu the Eder SVE pilot study
report, March 1995). No additional studies would be needed. The conceptual SVE design for
Lagoon No. 1 includes five SVE wells spaced approximately 200 feet apart and screened from
approximately 5 to 35 feet below the bottom of the lagoon. The SVE wells would be manifolded
into an equipment building which would house the SVE blower unit. The SVE wells could be
operated one at a time to minimize the size of the blower needed to remove the residual VOCs.
Wherever possible, NPI and Eder would select blowers and other equipment for the Lagoon No. 1
SVE system that could be used in the SVE system to be constructed at the MRDS in 1998. The
actual SVE system specifications would be determined during the design phase.
The SVE system would operate until the VOC vapors have been removed from the vadose zone.
The extracted soil vapors would be monitored to evaluate the reductions in subsurface soil vapor
VOC concentrations. With the waste forge compound removed from Lagoon No. 1, there should
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be no remaining source of VOCs besides the residual vapor phase VOCs. Once the vapor phase
VOCs are removed, the source of groundwater contamination should be eliminated. Assuming that
no source remains to generate additional soil vapor VOCs, the SVE system should operate for
several months to remove the residual VOCs. The actual time frame and operating schedule wouldbe determined by monitoring the VOC concentrations of the extracted vapors during SVE system
operation. The potential for VOCs to diffuse into soil vapor from the small amount of residual waste
forge compound mixed with soil at the bottom of the lagoon would be considered when designingthe SVE system and developing an SVE operating plan.
Effectiveness - The SVE alternative should effectively remove residual vapor phase VOCs from the
vadose zone to eliminate the low level source of groundwater contamination within several months,
assuming there is no remaining source of VOC vapors. Backfilling the lagoon would eliminatehuman health risks as described for the no further action alternative. The IRA extraction systemwould continue operating to prevent the off-site migration of VOCs in groundwater at concentrations
above the Wisconsin groundwater standards and protect the environment. The SVE alternative
should enable the IRA to be shut down in approximately 5 years since the source of contaminants
in the vadose zone should be eliminated. The actual time frame would be determined based on
groundwater monitoring results. Risks to workers during installation and operation of the SVE
system and placement of backfill in the lagoon would be addressed by a site-specific health andsafety plan. This alternative would meet the ARARs using SVE to remove vapor phase VOCs to
non-detectable levels and eliminate the residual low level source of VOCs to groundwater at the
lagoon area.
This alternative would achieve the remedial action objectives. The SVE system would remove
VOCs from the vadose zone and would be operated until vapor phase VOC concentrations reach
non-detectable levels. Treatment of the extracted VOCs would not be required to meet WDNR air
emission regulations given the low levels of VOCs that remain beneath the lagoon. This alternative
would also rely on continued operation of the IRA extraction system to prevent off-site migration
of VOCs in groundwater. SVE should eliminate the residual source of groundwater contamination
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at this area. The IRA system would be operated and maintained until VOC concentrations in on-site
groundwater at the Lagoon No. 1 area are reduced to below the PALs or to the lowest possible levels
below the MCLs and Enforcement Standards.
Implementability - This alternative is technically feasible. SVE systems are widely used to remove
VOCs from unsaturated soils. The fine grain sand at the NPI site is well-suited to effective SVEapplication, as demonstrated by the SVE pilot study conducted at the MRDS. Contaminant transport
modeling would not be required to develop NR 720 soil cleanup levels, since the SVE system would
be operated until VOC vapor concentrations are non-detect. SVE system samples would be
submitted to a laboratory for analysis. The Lagoon No. 1 SVE system would be designed based on
the MRDS SVE pilot study results and would be consistent with the full-scale MRDS SVE system
design. Equipment selected for the Lagoon No. 1 SVE system would be compatible with the MRDS
system wherever possible. It is expected that the SVE system could be installed and started up
within two months of USEPA approval. The equipment required for the SVE system is readily
available and could be installed by local contractors. No off-site treatment or disposal would be
required under this alternative.
No permits, easements or rights of way would be required to implement this alternative. There
should be no impacts on adjacent properties and no need for institutional controls.
Cost - The cost to design and install an SVE system at Lagoon No. 1, including backfilling, is
estimated at $480,000, as summarized in Table 13. The operation and maintenance costs would be
minimal given the short operating time estimated to remove residual VOC vapors from the vadose
zone.
4.1.3 Alternative V-3 - Composting in Biopiles
Under this alternative, soils would be removed from the vadose zone beneath Lagoon No. 1 for
composting. Composting is a controlled biological process by which biodegradable contaminants
are converted by microorganisms (usually indigenous microorganisms) to innocuous byproducts.
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Approximately 120,000 cubic yards of soil would be excavated from the bottom of the lagoon to
bedrock or groundwater, whichever is encountered first. The soil would be placed in windrows (long
piles) where it would periodically be mixed using mechanical equipment. A pilot study would be
required to evaluate the effect that biodegradation in the compost piles would have on VOC
concentrations and to determine whether non-detectable VOC levels can be achieved.
The treated soil would be returned to Lagoon No. 1 once the VOC concentrations are reduced to non-
detectable levels. The lagoon would then be backfilled to existing grade.
Composting should remove the residual VOCs that act as a low level source of groundwater
contamination. VOCs would not continue to leach to groundwater once they are removed. VOC
concentrations in on-site groundwater would reach the PALs or be reduced to the lowest levels
possible in significantly less time than the no action alternative, so the IRA system could be shut
down more quickly. The IRA system at the southwestern portion of the NPI site would operate for
an estimated five years under the composting alternative (source removed) versus ten years for the
no action alternative (source remains) (see Appendix C). The actual time frame would be
determined based on groundwater monitoring results.
Effectiveness - This alternative should remove residual VOCs from the vadose zone soils to
eliminate the low level source of groundwater contamination. A pilot study would be required to
determine how long the soil would have to remain in the biopiles in order to remove the residual
VOCs to non-detect levels (if possible) before it could be placed back into the lagoon. Backfilling
the lagoon would eliminate human health risks as described for the no further action alternative. The
IRA extraction system would continue operating to prevent the off-site migration of VOCs in
groundwater at concentrations above the Wisconsin groundwater standards and protect the
environment. The composting alternative should enable the IRA to be shut down in approximately
five years since the source of contaminants in the vadose zone would be eliminated. The actual time
frame would be determined based on groundwater monitoring results. Risks to workers during
excavation, placement and aeration of the soil in the biopiles, and placement of backfill in the lagoon
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would be addressed by a site-specific health and safety plan. This alternative may meet the ARARsusing composting to remove vapor phase VOCs to non-detectable levels and eliminate the residual
low level source of VOCs to groundwater at the lagoon area. A pilot study would be required to
evaluate the ability of this alternative to meet the ARARs.
This alternative would reiy on excavation and biodegradation to remove VOCs from the vadose zonesoils and achieve the remedial action objectives. The ability of this alternative to reduce VOC
concentrations to non-detectable levels and eliminate the residual source of groundwatercontamination at this area is uncertain. This alternative would also rely on continued operation of
the IRA extraction system to prevent off-site migration of VOCs in groundwater. The IRA system
would be operated and maintained until VOC concentrations in on-site groundwater at the Lagoon
No. 1 area are reduced to below the PALs or to the lowest possible levels below the MCLs andEnforcement Standards.
Implementabilitv - This alternative would be difficult to implement given the amount of soil
excavation required and the excavation depths (up to 60 feet) that would be involved. Specialized
excavation equipment and operators would be required to remove soil at significant depths.
Substantial land areas would be needed to compost the volume of vadose zone soil (estimated at120,000 cubic yards). A pilot study would be required to evaluate the effectiveness and
implementability of this alternative and to determine the remedial time frame. Additional actions
may be required if composting does not remove VOCs to non-detect levels. Soil samples from the
biopiles would be analyzed by a certified laboratory to determine the VOC removals achieved. The
mechanical equipment required to turn the biopiles is readily available and could be operated by
local contractors. No off-site treatment or disposal would be required under this alternative.
No permits, easements or rights of way would be required to implement this alternative. There
should be no impacts on adjacent properties and no need for institutional controls.
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Cost - The cost to design and implement a composing action for the Lagoon No. 1 vadose zone soils
is estimated at $10,500,000, as summarized in Table 14. This estimate includes maintenance of the
biopiles.
4.1.4 Alternative V-4 - Off-site Landfilling
Under this alternative, soils would be removed from the vadose zone beneath Lagoon No. 1 fordisposal in an off-site landfill. Approximately 120,000 cubic yards of soil would be excavated fromthe bottom of the lagoon to bedrock or groundwater, whichever is encountered first. The off-site
landfill would either comply with the NR 504 solid waste landfill requirements or the NR 660
hazardous waste landfill requirements. This alternative would be implemented based on ARARs.
The off-site landfill would be properly licensed and would operate in compliance with its permit and
applicable regulations. The off-site facility would be selected based on USEPA and WDNRrequirements and the willingness of the facility to accept material from a Superfund site for disposal.
The excavated soil would be hauled from the NPI site to the off-site landfill in accordance withapplicable waste generator and transport regulations, including manifests and other record keepingrequirements. Lagoon No. 1 would be backfilled following excavation of the soil. Approximately
170,000 cubic yards of material would be required to fill the lagoon 10 existing grade.
Excavation and off-site disposal would remove the residual VOCs that act as a low level source of
groundwater contamination. VOCs would not continue to leach to groundwater once they are
removed. VOC concentrations in on-site groundwater would reach the PALs or be reduced to the
lowest levels possible in significantly less time than the no action alternative, so the IRA system
could be shut down more quickly. The IRA system at the southwestern portion of the NPI site
would operate for an estimated five years under the off-site landfilling alternative (source removed)
versus ten years for the no action alternative (source remains) (see Appendix C). The actual time
frame would be determined based on groundwater monitoring results.
Effectiveness - This alternative would remove vadose zone soils containing VOCs from the lagoon
to eliminate the low level source of groundwater contamination and protect the environment. The
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human health risks posed by the residual VOCs would be eliminated by excavation and off-site
disposal. The IRA extraction system would continue operating to prevent the off-site migration of
VOCs in groundwater at concentrations above the Wisconsin groundwater standards and protect the
environment. The off-site disposal alternative should enable the IRA to be shut down in
approximately 5 years since the source of contaminants in the vadose zone would be eliminated. The
actual time frame would be determined based on groundwater monitoring results. Risks to workers
during excavation of the soil and placement of backfill in the lagoon would be addressed by a site-
specific health and safety plan. This alternative would meet the ARARs by removing the vadose
zone soil and eliminating the residual low level source of VOCs to groundwater at the lagoon area
to provide permanent protection.
This alternative would achieve the remedial action objectives. No residual VOCs would remain at
the lagoon area following excavation and off-site disposal. The soil would not be treated unless
required by the land disposal facility or to comply with ARARs. This alternative would rely oncontinued operation of the IRA extraction system to prevent off-site migration of VOCs in
groundwater. The IRA system would be operated and maintained until VOC concentrations in on-
„!*_ fcTOundwater at the Lagoon No. 1 area are reduced to below the PALs or to the lowest possible
levels below the MCLs and Enforcement Standards.
Implementabilitv - This alternative would be difficult to implement given the amount of soil
excavation required (estimated at 120,000 cubic yards) and the excavation depths (up to 60 feet) that
would be involved. Specialized excavation equipment and operators would be required to remove
soil at significant depths. It is estimated that this alternative could be implemented within
approximately four to six months of USEPA approval.
An appropriate off-site land disposal facility would be selected during design based on ARARs and
the willingness of the facility to accept materials from a CERCLA site for disposal. No laboratory
analysis of the soil is expected given the significant amount of data collected to characterize the
vadose zone beneath Lagoon No. 1. There are no operating hazardous waste landfills in Wisconsin.
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The environmental compliance status of the disposal facilities would be checked during the selection
process. The selected facility would have to be approved by USEPA in accordance with the
CERCLA Off-Site Policy and by WDNR if the facility is in Wisconsin. The soil would be
transported from the NPI site to the off-site landfill by a licensed waste hauler in accordance with
applicable regulations.
No permits, easements or rights of way would be required to implement this alternative. There
should be no impacts on adjacent properties and no need for institutional controls.
Cost - The cost to dispose of the vadose zone soil at an off-site landfill is estimated at $15,480,000,
as summarized in Table 15. This estimate assumes that the soil could be disposed of at a non-hazardous waste landfill and that treatment would not be required prior to disposal.
4.2 Stockpiled Waste/Soil
4.2.1 Alternative S-l - Consolidate Under MRDS Cap
Under this alternative, the stockpiled low BTU value waste/soil (approximately 10,000 cubic yards)
would be removed from the temporary storage area at the MRDS, consolidated with waste materials
from the East Disposal Site and Drainage Ditch 3, and capped at the MRDS. The MRDS will be
capped pursuant to the May 1996 ROD for the NPI site. An SVE system will also be installed at the
MRDS to provide additional protection against migration of VOCs beneath the cap. The MRDS
capping/SVE action is currently in the design phase, with construction planned for 1998. This
alternative would create a single waste management unit at the NPI site.
Effectiveness - This alternative would protect human health by capping to eliminate the direct
contact exposure pathway and achieve the remedial action objectives. The low BTU waste/soil
would be removed from the temporary stockpiles and consolidated in a single waste management
unit at the MRDS. The multi-layer cap to be installed at the MRDS would minimize leachate
generation and vertical migration of VOCs to groundwater to protect the environment. The cap will
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be constructed in compliance with ARARs pursuant to the May 1996 ROD. Risks to workers during
excavation of the stockpiles, placement of the low BTU waste/soil at the MRDS and construction
of the cap would be addressed by a site-specific health and safety plan.
This alternative does not include treatment of the waste/soil. The MRDS cap would cover and
contain the residual VOCs in this material to protect human health and the environment. Long-term
maintenance of the cap would ensure the integrity of the cap and continued environmental
protection. Deed restrictions would be established to prohibit future development on the capped
area.
Implementabilitv - This alternative is technically feasible. Capping is widely used to prevent contact
with waste materials and minimize leachate generation. The low BTU waste/soil is stored in
temporary stockpiles near the MRDS, which would expedite removal of this material forconsolidation at the MRDS in the initial stages of cap construction. It is expected that the waste/soil
could be moved to the MRDS in less than one month. The stockpiled waste/soil could be removed
from the temporary storage area and consolidated at the MRDS by local contractors using readily
available equipment. No laboratory analysis would be required before placing the waste/soil at the
MRDS. No off-site treatment or disposal would be required under this alternative.
No permits, easements or rights of way would be required to implement this alternative. There
should be no impacts on adjacent properties and no need for institutional controls. The need for
these items as they relate to construction of the MRDS cap will be addressed as part of the MRDS
cap/SVE design.
Cost - The cost to move the stockpiled waste/soil to the MRDS for consolidation and capping is
estimated at $100,000, as summarized in Table 16. There would be no operation and maintenance
associated with this alternative.
LLVS9SO WT 28
eder associates
4.2.2 Alternative S-2 - Soil Vapor Extraction
Under this alternative, the stockpiled low BTU value waste/soil (approximately 10,000 cubic yards)
would be removed from the temporary storage area at the MRDS and returned to Lagoon No. 1 fortreatment by SVE to remove VOCs as described for Alternative V-2. The lagoon would then be
backfilled to existing grade.
Effectiveness - Returning the stockpiled waste/soil to the lagoon for treatment by SVE would not
protect human health or the environment. The SVE pilot study conducted at the MRDS
demonstrated that SVE would not effectively remove VOC vapors from materials containing
significant amounts of waste forge compound (such as the stockpiled waste/soil) because sufficient
air flow cannot be established through the material. Therefore, it would not be feasible to use SVE
to remove VOCs from the stockpiled waste/soil. This alternative would not comply with ARARs.
This alternative would not achieve the remedial action objectives and there would be no risk to
workers since SVE is not a viable option to remove VOCs from the waste/soil. Residual VOCs
would remain in the material and act as a source of VOCs to groundwater. This alternative would
not provide any long-term protection.
Implementability - This alternative is not technically feasible. Although SVE systems are widely
used to remove VOCs from unsaturated soils, the MRDS SVE pilot study demonstrated that SVE
would not effectively remove VOC vapors from materials similar to the stockpiled waste/soil.
Because SVE is not a technically feasible option for the waste/soil, it is not appropriate to address
implementation time frames, equipment and labor requirements, and administrative concerns for this
alternative.
Cost - Costs have not been developed for this alternative since it is not technically feasible to use
SVE to remove VOCs from the stockpiled waste/soil.
LLVSMO RPT 29
eder associates
4.2.3 Alternative S-3 - Use as Supplemental Cement Kiln Fuel
Under this alternative, the stockpiled waste/soil (approximately 10,000 cubic yards) would be
removed from the temporary storage area at the MRDS and packaged in five- or six-gallon plastic
buckets for use as a solid supplemental cement kiln fuel. This alternative is the same as the Lagoon
No. 1 waste forge compound removal action conducted in November 1994 - December 1995. The
material would be characterized to determine if it meets the minimum 5,000 BTU/lb supplemental
fuel requirement before being packaged. The packaged materials (>5,000 BTU/lb) would be
transported to CERCLA-approved cement kilns which comply with USEPA's Off-Site Policy and
have been approved to accept Superfund wastes consistent with the facilities' operating permits. At
the kiln, the buckets would be fed into the cement kiln and burned as supplemental fuel after the kiln
verifies that the material meets the required specifications.
Effectiveness - The waste/soil removed from Lagoon No. 1 and stockpiled near the MRDS has
heating values below 5,000 BTU/lb. Because this material did not meet the minimum 5,000 BTU/lb
supplemental fuel requirement, it could not be packaged and sent to the cement kilns during the
waste forge compound removal action. This material was removed from the lagoon and stockpiled
to facilitate vadose zone sampling activities and final disposal pursuant to this EE/CA. The
stockpiled waste/soil does not have sufficient BTU value to be used as a supplemental cement kiln
fuel, so this alternative would not protect human health or the environment. This alternative would
not comply with ARARs.
This alternative would not achieve the remedial action objectives and there would be no risk to
workers since this option is not feasible. Residual VOCs would remain in the material and would
act as a source of VOCs to groundwater. This alternative would not provide any long-term
protection.
Implementabilitv - This alternative is not technically feasible because the stockpiled waste/soil does
not meet the 5,000 BTU/lb heating value required for supplemental cement kiln fuels. Therefore,
LLV5980 RPT 30
eder associates
it is not appropriate to address implementation time frames, equipment and labor requirements, and
administrative concerns for this alternative.
Cost - Costs have not been developed for this alternative since the stockpiled waste/soil does not
meet the minimum BTU requirement for supplemental cement kiln fuels.
4.2.4 Alternative S-4 - Off-site Landfilling
Under this alternative, the stockpiled low BTU value waste/soil (approximately 10,000 cubic yards)
would be removed from the temporary storage area at the MRDS for disposal in an off-site landfill.
The off-site landfill would either comply with the NR 504 solid waste landfill requirements or the
NR 660 hazardous waste landfill requirements. This alternative would be implemented based on
ARARs. The off-site landfill would be properly licensed and would operate in compliance with its
permit and applicable regulations. The off-site facility would be selected based on USEPA and
WDNR requirements and the willingness of the facility to accept material from a Superfund site for
disposal. The excavated soil would be hauled from the NPI site to the off-site landfill in accordance
with applicable waste generator and transport regulations, including manifests and other record
keeping requirements.
Effectiveness - This alternative would remove the stockpiled waste/soil from the temporary storage
area for off-site disposal to eliminate human health risks and protect the environment. Risks to
workers during removal of the stockpiled waste/soil would be addressed by a site-specific health and
safety plan. This alternative would comply with ARARs by removing the waste/soil for off-site
disposal to provide permanent protection.
This alternative would achieve the remedial action objectives. No residual VOCs would remain at
the waste/soil stockpile area following excavation and off-site disposal of the low BTU material.
The waste/soil would not be treated unless required by the land disposal facility or to comply with
ARARs.
LLVS9IO RPT 31
eder associates
Implementabilitv - This alternative couid be implemented using local contractors and equipment to
remove the waste/soil from the temporary stockpiles. Off-site land disposal of wastes and soil is a
commonly used option. It is estimated that this alternative could be implemented within
approximately four to six months of USEPA approval.
An appropriate off-site land disposal facility would be selected during design based on ARARs and
the willingness of the facility to accept materials from a CERCLA site for disposal. Laboratory
analysis may be required to characterize the waste/soil prior to acceptance by an off-site facility.
There are no operating hazardous waste landfills in Wisconsin. The environmental compliance
status of the disposal facilities would be checked during the selection process. The selected facilitywould have to be approved by USEPA in accordance with the CERCLA Off-Site Policy and by
WDNR if the facility is in Wisconsin. The waste/soil would be transported from the NPI site to theoff-site landfill by a licensed waste hauler in accordance with applicable regulations.
No permits, easements or rights of way would be required to implement this alternative. There
should be no impacts on adjacent properties and no need for institutional controls.
Cost - The cost to dispose of the waste/soil at an off-site landfill is estimated at $1,130,000, as
summarized in Table 17. This estimate assumes that the waste/soil could be disposed of at a non-
hazardous waste landfill and that treatment would not be required prior to disposal.
LLVS9IO RPT 32
eder associates
5JL COMPARATIVE ANALYSIS OF REMEDIAL ALTERNATIVES
The remedial alternatives evaluated in Section 4.0 are compared based on effectiveness,implementability and cost. The comparison is presented separately for the vadose zone soil and the
low BTU value stockpiled waste/soil.
5.1 Vadose Zone
Effectiveness - All of the alternatives would protect human health and the environment by
eliminating direct contact with contaminants (by backfilling or off-site disposal) and removing
VOCs from the vadose zone to achieve the remedial action objectives. Under the no further action
alternative (Alternative V-l), vadose zone vapor phase VOCs in the residual waste materials could
continue to migrate and act as a low level source of contaminants to groundwater.
The no further action alternative (Alternative V-l) would rely on uai^ai attenuation to comply with
ARARs over the long term. Under this alternative, natural flushing would wash residual vapor phase
VOCs out of the vadose zone over time and into groundwater to eliminate the residual source of
groundwater contamination over the long term.
The SVE alternative (Alternative V-2) should effectively remove residual vapor phase VOCs from
the vadose zone to eliminate the low level source of groundwater contamination within several
months, assuming there is no remaining source of VOC vapors. The actual SVE operating time
frame would be determined based on system monitoring results. This alternative would meet the
ARARs using SVE to remove vapor phase VOCs to non-detectable levels. Treatment of the
extracted VOCs would not be required to meet WDNR air emission regulations given the low levels
of VOCs that remain beneath the lagoon.
LLVS9IO RPT 33
eder associates
The composting alternative (Alternative V-3) should remove residual VOCs from the vadose zone
soils to eliminate the low level source of groundwater contamination. A pilot study would be
required to evaluate the ability of this alternative to meet the ARARs and to determine how long the
soil would have to remain in the biopiles in order to remove the residual VOCs to non-detect levels
(if possible) before it could be placed back into the lagoon. The ability of this alternative to reduce
VOC concentrations to non-detectable levels and eliminate the residual source of groundwater
contamination at this area is uncertain.
The off-site landfilling alternative (Alternative V-4) would remove vadose zone soils containing
VOCs from the lagoon to eliminate the low level source of groundwater contamination and protect
the environment. The human health risks posed by the residual VOCs would be eliminated by
excavation and off-site disposal. This alternative would meet the ARARs and provide permanentprotection. No residual VOCs would remain at the lagoon area following excavation and off-site
disposal. The soil would not be treated unless required by the land disposal facility or to comply
with ARARs. This alternative would pose a risk to the community since the waste/soil would have
to be transported to the selected off-site disposal facility.
Under all of the vadose zone alternatives, the IRA system would be operated and maintained until
VOC concentrations in on-site groundwater at the Lagoon No. 1 area are reduced to below the PALs
or to the lowest possible levels below the MCLs and Enforcement Standards. If the low level source
of VOCs is not removed (Alternative V-l), the IRA extraction system would continue operating for
an estimated 10 years to prevent the off-site migration of VOCs in groundwater at concentrations
above the Wisconsin groundwater standards and protect the environment. The other alternatives (V-
2, V-3 and V-4) include source removal by on-site treatment or off-site disposal and should enable
the IRA to be shut down in approximately 5 years since the source of contaminants in the vadose
zone would be eliminated. The actual time frame would be determined based on groundwater
monitoring results.
LLVS980 RPT 34
eder associates
Risks to workers under all of the alternatives would be addressed by a site-specific health and safety
plan. The worker exposures posed by Alternatives V-3 and V-4, which include the removal of an
estimated 120,000 cubic yards of soil from the vadose zone are significantly greater than
Alternatives V-l and V-2, where the soil would remain in place.
Implementabilitv - The no action (Alternative V-l) and SVE alternatives (Alternative V-2) could
be implemented with little difficulty since the vadose zone soil would remain in place. The
composting (Alternative V-3) and off-site landfilling alternatives (Alternative V-4) would be much
more difficult to implement given the amount of soil excavation required (estimated at 120,000 cubic
yards) and the excavation depths (up to 60 feet) that would be involved. Specialized excavation
equipment and operators would be required to remove soil at significant depths.
The no action alternative (Alternative V-l) is technically feasible and could be readily implemented
by NPI or a local contractor using suitable on-site materials as backfill. Backfill material could also
be imported if needed. Materials would be sampled and characterized by a certified laboratory
before being used as backfill. The lagoon could be backfilled within approximately two months ofUSEPA approval.
Contaminant transport modeling to develop NR 720 site-specific soil cleanup levels and support the
no action alternative would require many assumptions and it is probable that the modeling would
not conclusively demonstrate that the concentrations of residual vapor phase VOCs in the vadose
zone would not cause the groundwater standards to be exceeded.
The SVE alternative (Alternative V-2) is technically feasible. SVE systems are widely used to
remove VOCs from unsaturated soils and the fine grain sand at the NPI site is well-suited to effective
SVE application. Contaminant transport modeling would not be required to develop NR 720 soil
cleanup levels, since the SVE system would be operated until VOC vapor concentrations are non-
detect. The Lagoon No. 1 SVE system would be designed based on the MRDS SVE pilot study
results and would be consistent with the full-scale MRDS SVE system design. It is expected that
LLV59BO RPT 35
eder associates
the SVE system could be installed and started up within two months of USEPA approval. The
equipment required for the SVE system is readily available and could be installed by local
contractors.
Under Alternative V-3, substantial land areas would be needed to compost the soil removed from
the vadose zone. A pilot study would be required to evaluate the effectiveness and implementability
of this alternative and to determine the remedial time frame. Additional actions may be required if
composting does not remove VOCs to non-detect levels. The mechanical equipment required to turn
the biopiles is readily available and could be operated by local contractors.
Under Alternative V-4, an appropriate off-site land disposal facility would be selected during design
based on ARARs. It may be difficult to locate a facility that is willing to accept materials from a
CERCLA site for disposal. No laboratory analysis of the soil is expected given the significant
amount of data collected to characterize the vadose zone beneath Lagoon No. 1. There are no
operating hazardous waste landfills in Wisconsin. The selected facility would have to be approved
by USEPA in accordance with the CERCLA Off-Site Policy and by WDNR if the facility is in
Wisconsin. The soil would be transported from the NPI site to tht off-site landfill by a licensed
waste hauler in accordance with applicable regulations. It is estimated that Alternative V-4 could
be implemented within approximately four to six months of USEPA approval.
No permits, easements or rights of way would be required to implement any of the vadose zone
alternatives. There should be no impacts on adjacent properties and no need for institutional
controls.
Cost - The costs associated with the composting (Alternative V-3) and off-site landfilling
alternatives (Alternative V-4) are 20 to 30 times more than the SVE (Alternative V-2) costs. These
alternatives (V-3 and V-4) are not cost-effective.
LLV59M RPT 36
eder associates
Under the no action option (Alternative V-l), contaminant transport modeling would be required at
a cost of approximately $40,000 in an attempt to demonstrate to USEPA and WDNR that the levels
of residual VOCs in the vadose zone beneath Lagoon No. 1 would not contravene the PALs in
groundwater. Annual O&M and monitoring for the IRA system at the southwestern portion of the
NPI site would cost an estimated $400,000 over the estimated ten years until the system can be shut
down.
Under the SVE option (Alternative V-2), an SVE system would be designed and installed for
approximately $180,000, with an additional $300,000 associated with backfilling the lagoon after
SVE operation is complete. SVE operating costs should be minimal if there is no remaining source,
since the VOC vapors should be removed in approximately one month. Annual O&M and
monitoring for the IRA system at the southwestern portion of the NPI site would cost an estimated$200,000 until the system can be shut down (estimated at 5 years). This O&M cost is half of the cost
under the no action option since the IRA system should be shut down much sooner if the low level
source of groundwater contamination is removed using SVE.
5.2 Stockpiled Low BTU Waste/Soil
Effectiveness - Consolidating the waste/soil at the MRDS for capping (Alternative S-l) to create a
single waste management unit at the NPI site would protect human health by eliminating the direct
contact exposure pathway. The multi-layer cap to be installed at the MRDS would minimize
leachate generation and vertical migration of VOCs to groundwater to protect the environment. The
MRDS cap would cover and contain the residual VOCs in this material to protect human health and
the environment. Long-term maintenance of the cap would ensure the integrity of the cap and
continued environmental protection.
The off-site landfilling alternative (Alternative S-4) would also eliminate human health risks and
protect the environment. This alternative would comply with ARARs by removing the waste/soil
for off-site disposal to provide permanent protection. No residual VOCs would remain at the
LLV5980 RPT 37
eder associates
waste/soil stockpile area following excavation and off-site disposal of the low BTU material. The
waste/soil would not be treated unless required by the land disposal facility or to comply with
ARARs.
Alternatives S-l and S-4 would achieve the remedial action objectives and risks to workers would
be addressed by a site-specific health and safety plan. The landfilling alternative would pose a risk
to the community since the waste/soil would have to be transported to the selected off-site disposal
facility.
Neither the SVE (Alternative S-2) nor the supplemental cement kiln fuel alternative (Alternative S-3)
would be a viable option to remove VOCs from the waste/soil. These alternatives would not achieve
the remedial action objectives or ARARs. The SVE pilot study conducted at the MRDS
demonstrated that SVE would not effectively remove VOC vapors from materials containing
significant amounts of waste forge compound (such as the stockpiled waste/soil) because sufficient
air flow could not be established through the material. The waste/soil removed from Lagoon No.1 and stockpiled near the MRDS does not meet the minimum 5,000 BTU/lb supplemental fuel
requirement.
Implementabilitv - Consolidating the waste/soil at the MRDS for capping (Alternative S-l) is
technically feasible and could be readily implemented. Capping is widely used to prevent contact
with waste materials and minimize leachate generation. The low BTU waste/soil is stored in
temporary stockpiles near the MRDS, which would expedite removal of this material for
consolidation at the MRDS in the initial stages of cap construction. It is expected that the waste/soil
could be moved to the MRDS in less than one month by local contractors using readily available
equipment. No laboratory analysis would be required before placing the waste/soil at the MRDS.
Off-site landfilling (Alternative S-4) is also technically feasible, but could not be implemented as
easily as waste consolidation at the MRDS since the waste/soil would be disposed of off-site. An
appropriate off-site land disposal facility would be selected during design based on ARARs. It may
LLVS9IO RFT 38
eder associates
be difficult to locate a facility that is willing to accept materials from a CERCLA site for disposal.
Laboratory analysis may be required to characterize the waste/soil prior to acceptance by an off-site
facility. There are no operating hazardous waste landfills in Wisconsin. The selected facility would
have to be approved by USEPA in accordance with the CERCLA Off-Site Policy and by WDNR if
the facility is in Wisconsin. This alternative could be implemented using local contractors and
equipment to remove the waste/soil from the temporary stockpiles. It is estimated that this
alternative could be implemented within approximately four to six months of USEPA approval.
No permits, easements or rights of way would be required to implement Alternatives S-l and S-4.
There should be no impacts on adjacent properties and no need for institutional controls.
Neither the SVE (Alternative S-2) nor the supplemental cement kiln fuel alternative (Alternative S-3)
is technically feasible, thus it is not appropriate to address implementation time frames, equipment
and labor requirements, and administrative concerns for these alternatives.
Cost - Cost estimates were not developed for the technically infeasible alternatives (S-2 and S-3).
Consolidating the stockpiled waste/soil at the MRDS (Alternative S-l) would cost approximately
$100,000. Off-site landfilling (Alternative S-4) would cost over ten times more than waste/soil
consolidation at the single waste management unit at the NPI site.
LLVS9IO RPT 39
eder associates
6.0 RECOMMENDED REMEDIAL ALTERNATIVE
Based on this evaluation, NPI and Eder recommend the following remedial actions:
• Installing an SVE system to remove residual vapor phase VOCs from the vadose
zone beneath Lagoon No. 1, and
• Consolidating the stockpiled low BTU waste/soil for capping at the MRDS.
The composting and off-site landfilling alternatives for the vadose zone would not be cost-effective
compared to SVE and would not be feasible given the implementation difficulties associated with
removing the significant volume of vadose zone soil. Although both the no further action option and
the SVE option would ultimately remove residual VOCs from the vadose zone, the SVE option
should accomplish this within a matter of months as compared to years under no action. The SVE
option should results in a significant savings in IRA system operation and maintenance costs over
the long term compared to no action. The SVE option would not involve development of NR 720
soil cleanup levels. Contaminant transport modeling to support the no action alternative would
require many assumptions and it is probable that the modeling would not conclusively demonstrate
that an SVE system is not necessary.
Neither SVE nor use as a supplemental cement kiln fuel would be technically feasible options for
the stockpiled waste/soil. Off-site landfilling would not be cost-effective compared to waste/soil
consolidation at the MRDS. Consolidation and capping the waste/soil at the MRDS is the only
reasonable method to dispose of this material, since the remainder of the waste forge compound-
containing materials at the NPI site will be consolidated and capped in a single waste management
unit at the MRDS pursuant to the May 1996 ROD.
LLVS9JO JUT 40
eder associates
NPI and Eder are prepared to quickly design and install the Lagoon No. 1 SVE system in 1997, upon
approval from USEPA and WDNR. The stockpiled waste/soil would be removed and consolidated
at the MRDS in step with installation of the MRDS cap planned for 1998.
LLVS9IO R?T 41
DDr"mC/)
NATIONAL PRESTO INDUSTRIES, INC.EAU CLAIRE, WISCONSIN
TABLE I
Summary of VOCs Detected in Soil Samples - 1995
TARGET COMPOUND(Units in u^/k^l
SITE ID:
SAMPLE ID:
DATE COLLECTED:
DKPTII(fl):SAMPLE DELIVERY GROUP;
Acetone
2-Buianune
1,2-Dichloroethanc
Mkxunoni:
Mcih> lent diluritkretrachluroeltiene
lolucnc1 , 1 , 1 -TridiltmiclhaiK:
rtithlofoelhcne
B-lU- 1-0
8/3U/95
0
B-l-0
< 1 300 U
1600 B
< 1300 U
< 1300 II
< 1 300 U
< 1300 U
1300 U
< 1300 11
< 1300 U
B-IB 1 10
8/30/95
10
11 1 10
< 10 U
< 10 11
< 10 11
< 10 II
< 10 II
< 10 11
< 10 II
< 10 U
< 10 U
B-lB 1-17
8/30/95
17
B-|. 10
< II U
< If U
< II uII II3 JB
< II II
< II U
< II I)
< II II
B-l
B 1 21
8/30/95
21
B 1 10
< 10 U
< 10 U
< 10 II
< 10 H
3 JB
< 10 U
< 10 11
< 10 II
< 10 U
B-l
B-l -23
8/ JO/9 5
23B 1-0
< 10 U
< 10 II
< 10 II
10 (1
3 Jll
< 10 U
<. 10 U
< 10 U
< ni ii
CDaCD
TABLE! XLS f*$t I of 11
NATIONAL PRESTO INDUSTRIES, INC.EAU CLAIRE, WISCONSIN
TABLE I
Summary of VOCs Detected in Soil Samples - 1995
TARGET COMPOUND(Uni t s in uc /kn )
SITE ID:SAMPLE ID:DA It COU-ttTEU:DEPTH (ft):SAMPLE DELIVERY GROUP:
Acelone2-HuUirumc
1,2-Oidiloroeihanc2-lk*x;in(inc
Mclhylciii.' chloride
I'uriidilimhMhene
liiluL-inj
1 ,1 ,1 -Trichlorttclhiim-IVichlonielhene
B-1B-I-23D8/ JO/95
23B I O
< 10 U
3 JI1< 10 II< 10 11
< 10 U< 10 I)
< 10 II
< 10 (1
< 10 U
B-l
B 1 25
8/30/95
25H 1 10
12
< 10 U
< 10 1)< 10 II
< 10 U
< 10 11•; II) II
< 10 If< II) 1 1
B-lB-l -27
8/30/9527
B-l-10
< 10 U
< 10 11
< 10 (1
5 J< 10 11
< 10 II
I I I I I10 11
< 10 U
B-l
B-l -298/30/95
29
B 1 10
I S2 J
< II 11
< II U< II U
< II U
< I I I I< II 11< I I I I
B-l
B-l 338/30/95
33
B 1 10
< 10 U
2 I<• 10 II
< II) 11
< 10 II
< 10 U
10 II< 10 (1
10 I/
I'Alil til XI S Pine 2 of 11
CDato~1
0)(ftwoo0)"I—t(DW
NATIONAL PRESTO INDUSTRIES, INC.HAD CLAIRE, WISCONSIN
TABLI; I
Summary of VOCs Detected in Soil Samples - 1995
TARGET COMIMHIND
(('nils in UK !•«)
SITE 10:SAMI'I KID:
DAItrOI.l.EC IED:
DEF I'll (h):
SAMPl.i: DM.IVEKV KKOIIP:
Acetone
2-HuiaiNinc
1 ,2-DidilimielhaiK1
.2-lkx;iiiinii:
tfclhjtuic chloride
reiraLhlornelhcne
Toluene
1 .1 ,1 -1 iicnluroelhaiii-
Trichloroeihene
B 1
B-I-JI
K/JI/95
Jl
B-434
< 10 U
HI II10 II
< 10 I)
10 11
< 10 U
10 II
< 10 II
10 1 1
B-2
B-2-0
8/ju/ysU
B-l 10
1210 II
< 10 U
10 II
10 II
2 1
< 10 U< 10 II
3 J
B-2
B-2-S
S/30/95
5HI ID
II
II II
11 II
II II
II U
-N
15
21If) J
B-2B 2 10
s/jo/ysMl
B 1 10
10 J
< II (I
<: II (1
< II U
< II 11
< II (1
< II U
< II II< II 11
B-2
B MOD
8/30/95
10
B 1 10
12
II II
< II II
11 II
II II
II II
11 U1 1 I /
II (I
V21/97 TABLE) XLS Page J of 11
CDa(D-1
0)COWOOCD'i-+03W
eder associates
u5/3 -,LU Z
to O5 uO co*i2sto £S 2a- U
< r:
-JCQ
CLEn
CO
'o
CJO
^ NATIONAL PRESTO INDUSTRIES, INC. —EAU CLAIRE, WISCONSIN
TABLE I
Summary of VOCs Detected in Soil Samples - 1995
TARGET COMPOUND(Units in iin/ki;)
SITE ID:
SAMPLE ID:
DATE COLLECTED:
MM'MMfU;
SAMPLE ItELIVEHV GROUP:
Acelone
2-Buianonc
t,2-l)idilim>ethanc2-lle\aru>ik:
Mclhyknt; chloride
Iclrjchlorocihcni'
lul nun'
1 . 1 . 1 -Tnchlurucili.iiicI richloroethene
B-J
B-J-7D
8/31/957
11-13-1
10 J
<: 10 11
< 10 1)
< JO (J
< 10 U
< 10 1)
10 a< 10 U< 10 11
B-3
B-J-98/31/95
!*
b J J4< 10 |J
< 10 (1
< in u< I(J U
< 10 (1
< 10 U
- 10 II
10 (J
< 10 U
B-3
B-3- II
8/31/95
II
B-4-34
11< 10 11
< 10 U
< 10 U
< 10 U10 II
10 11
< 10 11
< 10 II
B-3
B-3 13
8/31/9513
B-434
< 10 U
< 10 11
< 10 1 1
< 10 II
< 10 II
< III II< 10 U
< 10 U
< |0 U
B-3
B-3 15
8/3l/y5
15
B-4-34
< 12 1)< 12 U
12 11
12 II
< 12 11< 12 U
< 12 II
< 12 U
< 12 II
S/II/97TABLEI XLS S of 11
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NATIONAL PRESTO INDUSTRIES, INC.EAU CLAIRE, WISCONSIN
TABLE I
Summary of VOCs Detected in Soil Samples - 1995
TARGET COMPOUND
(I'nils in uj; I-K)
SITE ID:SVMI'll II):
l»ATi: COLLECTED:
H K I ' H I ( f l ) :SAMPLE I)E 1 IV tKV GROUP:
AceloneMluliinone
l .2-l>iLh!oroeinanc2-Ilcxannne
Mclhyknc chloride
fclrachliiroelhene
lulucne
1,1,1-Trichloroeihanc
rrichhmtelhene
B-J
B-3-178/31/95
17
B-4 -34
265 J
< 10 II
< 10 I)
< 10 1110 11
10 II
< 10 11< 10 11
B-3
B-J- 198/3l/y5
19B J-34
< 10 U
< 10 II
< 10 11
1 0 I I
< 10 II
< 10 U
< to u< 10 II
< 10 U
B-4
B-4-S
8/31/95
50-1-0
< 1300 U
1 700 £1
1300 11
1300 II< 1300 1)
< 1300 (/
< 1300 U
< 1300 II< 1300 II
B-4B 4 10
8/31/95
10
B-l 0
< 1300 U
1600 H
< 1300 11
< 13(10 II
310 J< 130(1 II< 1300 II< I30D U< 1300 U
B-4
11-4-15
8/31/95
15B 1-0
< 10 (I
10 II
< 10 [I
10 II3 jn
< 10 I!
10 1 1
10 II< 10 U
0)a0)
S/2l.'S7TABLtl X1.S Pigc 6 of 11
NATIONAL PRESTO INDUSTRIES, INC.1-AU CLAIRE, WISCONSIN
TABU; i
Summary of VOCs Detected in Soil Samples- 1995
TARGET COMPOUND(Units in ut-/ku)
SITE ID:
SAMPLE II):
DATE COLLECTED:
DEPTH (ft):SAMPLE DELIVER*' GROUP:
Acetone
2-Hulaniinc
t.2-I)idiloroethanu
.Mkx.ijiiitic
V1clh)knc Lliluridi.
1 UrachUirutthcnc
lukiLiic
1 . 1 , 1 - liidilorocltKuiL
Iridilornclhene
B-4
it -1-20
8/31/95
20
[Ml!
< II) U
< 10 U
10 U
10 (i
1 Jit< 10 [1
< 10 (1
< 10 II
< in 11
B-4
B-4-25
8/3I/V525
111 U
< 10 If
< 10 II
< 10 II
10 II
) IK
< 10 II
< 10 U
< 10 11
-- 10 II
B-4
B-4 25D
8/31/9$
25
B-l-0
< 10 U
10 1110 U
10 U
1 Jit10 U
10 II
•= 10 II
ID II
B-4
B 4 28
8/31/^528
B I O
11 B
< 10 II
< 10 II
10 If
< JH
< 10 II
< 10 II
< 10 U
< 10 II
B-4
B-4-JU
8/JI/95
JO
Ul(l
< 10 U
10 [1
10 II
< 10 II
2 Jit
10 II
< 10 U
< 10 U
10 tl
1AH1 LI XI H P«g* 7 of M
Q.CD-iQ)W(/)Oo0)l-f0)CO
N A T I O N A L PRESTO INDUSTRIES, INC.LAU CLAIRE, WISCONSIN
TABLE I
Summary of VOCs Delecled in Soil Samples - 1995
TARGET COMPOUND
(Units in u^/kt-}
SITE ID:
SAMPI t H>:
DATE COLLECTED:
DEPTH (ft):
SAMPLE DELIVEKY GROUP:
Acetone
2-Hul;iiuinc
1,2-Dichlnruelhane
3-Hexani>neMclh) luiic chloritk-
relrachlomeihene
Toluene
l.l.l-'lriJiloroeihaiii:
rrichlorocihenc
B-4
B4-32
8/31/95
32B I O
17 B
1 Jll
< 10 U
< 10 (I< 10 11
< 10 I!
< 10 U< 10 U
< 10 U
B-4
11 4 34
8/31/95
34
B 4 3 4
13
3 J
< 10 II
< 10 II
< 10 U
< 10 U< 10 II
< 10 II
< 10 II
B-4
114-36
8/31/95
36H I D
< 10 U
<• 10 u<- 10 tl
10 h1 Jit
< t(l I!
< 10 II
< 10 U< 10 U
B-5
B-5-2
8/31/95
2
B-I-IO
< 10 tJ
< 10 11
< 10 tl
< 10 1!
< 10 U
< 10 U
< 10 U
< 10 U
< 10 II
B-5
B-5-7
8/JI/95
7
HH)
< 10 U
< 10 [I
< 10 If
10 It
10 [1
< 10 II
10 II
< 10 U
< 10 II
i / I IWTABl-fcl XI-S Pigt I of 11
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NATIONAL PRESTO INDUSTRIES, INC.KAUCI.AIRI- , WISCONSIN
TABI.L 1
Summary of VOCs Detected in Soil Samples - 1995
TARGET COMPOUND(Units in un'kg)
SITE ID:
SAMPLE ID:
DATECOI.LrtCTIlD:
DEP Til (fll:
SAMI'l.t ntUVtHV<;ROIU>:
A Cell UK'
2-Hutdiioiic
l,2-l)ichli)roelhanc
2-llcxjiiuni;
Vlclh) ICIIL' chloride
lelrach'nrncilieni.'
Toluene
I.IJ-Tndiloroelh.iiH
rrichlnroelhene
B-5
B5 22
8/31/95
2211 1 JO
< 10 II
< 10 1 J
< to u< 10 II
< II) 11< 10 II
< ni u< 10 a
10 U
B-7
B-7-0
8/31/95
0
B I O
< 10 U
10 U
- 10 II
10 11
•1 Jll< 10 II
< 10 11
< 10 II
1 J
B-7
B7-5
8/JI/95
5H 1 II
< 10 U
< 10 H
< 10 II
10 (1
J Jll< 10 II
< JO (1
10 1 1
10 II
B-7
B7-IO
8/JI/95
1(1It 10
< 10 U
< 10 II
< I!) I/
< 10 II
< 10 II
< 10 U
< 10 II
< 10 11
< 10 II
B-7
B-7- 101)
8/31/95
Ml
U 1 0
< 10 U
< 10 II
10 II
< 10 11
) JH
10 II
|{) U
10 II
< 10 U
0)a0)
S/2l '97TAflLEI XL5 Pigc 10 of 11
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NATIONAL PRESTO INDUSTRIES
EAU CLAIRE. WISCONSIN
TABLE 2
PGC ANALYTICAL RESULTS FOR SOIL VAPOR EXHAUST SAMPLES(ipproximately live feel below grade)
Sample ID. :
B-l
B-2B-3B-4B-5B-6B-7
Sample Date:
09/07/95
09/07/95
09/07/95
09/07/95
09/07/95
09/07/95
09/07/9
I.l.I-TCA
I9S20
12705
48630
91410
2387547417
ND
TCE
97
54
201
472
80
136199
PCE1 6 1
179484
332135
15659
NOTES.ND - Not DetectedAll concentrations are in ppb.
05/21.^7 VI \HYDRO\PROJECTS'.Q-tlXrS 0497\VALDTBLS\TABLE2 W0:
NATIONAL PRESTO INDUSTRIES, INC.LAUCI.AIRH, WISCONSIN
Summary of VOCs Detected in Soil Samples - 1996
lARGbl COMl'OUNU
(units in iijr'kg)
SITE:
SAMPLKID:I>A 1 fc COU.tCTliDAVi:KAfil: DEPTH (11)
SAMI'IMJH JVI KYOROlir
Acetone2-Bufanonel.l-DichloroelhaiKM-DichlurocthciK.-V4elh)lcnc uhloriiK-rcirachltiroeihuii1
1,1,2,2- 'Jciufliltiroi-iluneI'ulucncfrich Ion AtheneXylentftoial)
B-088 5 - 1
y/ 19/46075118
3411 UII [IIt UII U•J }II (IIJ II1 1 U5 J
B-08865 -7
9/IW966751)8
< 26 I)< 2h II
26 U< 26 II< 26 H
110< 26 11< 26 IJ
12 J< 26 11
B-08811-12y/ 1 >j/%
II 51)8
< 10 U< II) 1)
10 fl
< 10 H
10 IIID II
< ID U
< 10 U10 [1
10 U
B-08
8205-2)9/1 W%
2075
B8
< 10 U< 10 11
< 10 U< 10 U< in u
10 11
< 10 I)< 10 U< 10 U< 10 U
B-088305-31y/i'j/%
.10 75
U8
< 10 U< 10 U
< 10 U< 10 U< 10 II
10 II
< 10 U< 10 IJ< 10 II
10 U
<DQ.CD
V2I/V7 TABLE! Xl.S Pigelof 16CDw
NATIONAL PRESTO INDUSTRIES, INC.EAU CLAIRE, WISCONSIN
TABLE 3
Summary of VOCs Delecled in Soil Samples - 1996
TARUin I'OMI'itUND(units in i^'kj?)
SITESAMPLE ID;OAn-COLLECIlPAVCKAGI- I)HPIM(ti)SAMPLE DEI.IVTRY GROUP
Acelone2-Hutanonel.l-[)jdiloroelhancIJ-Didiloroclhcni'vtelhyluie cnlorulirciractiKiroclhencl,l,2,2-TelraLhlnrin:ihjnell)IULT1t
Irichlofoethene\>|L-IH; fiolal)
B-088405-41WIM/%4075
(18
< 10 U10 U10 U10 U10 (Ito U10 11
to uto u10 11
B-088505-519/ 1 'J/<>6
50.75Ha
< 10 U< 10 U< 10 U< 10 II
< 10 U< 10 (1< 10 U< 10 U< 10 U< JO II
B-08860-60 5')/ 1 '>/%
6025UK
< 11 U< M 11
II UII U
< 11 II11 UM U11 U11 (1II II
B-0991-1 59/1 y/%
1.25US
< 54 U< 54 U
60< 54 II< 54 11
320< 54 I)
IS i26 J
< 54 U
B-09955-6
9/ 1 W>65 7 5US
< 11 U< 11 II
5 J< 11 I)< 11 U
6111 U
< II U5 J
< II II
CDQ.0)-i0)M(/>0o
NATIONAL PRESTO INDUSTRIES, INC1
CAUCI .AIRH, WISCONSIN
I ABU: 3
Summary of VOCs Detecled in Soil Samples - 1996
lAkGhlUlMI'oUNI)(uniis in ui1 M:)
Aceione2-HiUaimne
1 1 -On lilotncllj.ini1,1 -l)iJilimH.'ihuicMeihykne chloriik-cinicliltiniclhcnc
.1 .2.-'- IcIraclilDiiu-ili.inc
I'oluaiL1
1 ridiliimclliuiiL-
Xylcne (lolal)
SITE:SAMI'I.MDDAM: COM fit 11:0AVI-KAGI- DEPTH (ft)SAMPLE DM IVi:KY(iROUP
B-099 1 0 5 - 1 2
W 1 7/96II 25HI9A
10 U
10 II
Ml U10 tl
10 II
10 (1
10 II
10 U
10 ('10 (1
B-0992 1 -2 1 5
21 25HH
< 10 U10 (1
•- 10 II
10 U
< 10 II
10 11< 10 II
< 10 11
< 10 11< 10 II
B-09y j 1 - 3 1 5
31 25It*
< 10 U10 II
10 (I
10 II
II) II10 II
10 II
10 U
10 II
10 II
B-099405-41y/w/%4075us
< 10 II
10 II
< 10 tl
< 10 II
< 10 tl
10 II
< 10 U
< 10 II
< 10 II
< 10 U
B-09
950 5 - 5 1y/l'J/96
5075US
< 10 II10 II
< 10 II
10 tl
10 |l
10 U
< 10 II
10 (I
10 II
10 tl
0)aa>-i0)wwOoQ)'•-+CD
J/21/yJTAIil t3 Xl.S P»ge Jof 16
NATIONAL PRESTO INDUSTRIES, INC.EAU CLAIRE, WISCONSIN
TAULL3
Summary of VOCs Delecled in Soil Samples - 1996
TARGET COMPOUND(units in uiVkj;)
SITE:SAMPLE ID:IMTECOLI.LCiliU
AVERAGE DEPTH (11):SAMPIEDUI IVKRYCROUI'.
Acetone2-Ruianonel.l"[)ichloroethatiL'l.l-DidiloroelhencMeihjleni: chlnmltrelradiloroethuif1.1.2.2-Tclnidilf'i^-tli.irie
TolueneCrichloructhcneXylenc (luial)
B-IO
101-1.50/19/96
1 251)8
< 10 U
< 10 U< 10 [1< 10 I)
10 U10 I)
Id U< 10 U< 10 U
10 U
B-IO1055-69/1 y/%
5 7 5MX
< 10 U< 10 1)< 10 If< 10 i;< 10 II< 10 11
< 10 H
< 10 U< 10 U< 10 II
B-10
1010-11.5y/ii>'(J6
1075
its* 10 U< 10 U- 10 U< 10 U< 10 (1
< 10 U10 U
< 10 U< 10 U< 10 U
n-Ki1021-21 59/iy/yo21 25
1(8
< 10 U
< 10 U< 10 U< 10 II< 10 II< 10 II
< 10 U< 10 U< 10 U< 10 U
B-IO1031 -.11 59/17/96
31 25
UI9A
< - 10 1)< |0 II
10 II< 10 (I< 10 II
10 11
< 10 (110 II
< 10 11< 10 11
P*K(4of 16
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— NATIONAL PRESTO INDUSTRIES, INC. ~~f - A U C I , A I K f : , WISCONSIN
TABU: 3
Summary of VOCs Detected in Soil Samples - 1996
lARGlTC COMPOUND(unils in uji'kg)
SITE:SAMPLE ID:DATE COU.ECI f:UAVERAGE DEPTH (ft)SAMPLCPn IVCRY GROUP
Acetone2-Hulanone1,1-Dichloroclhiitn1
IJ-DichloroeihcncVlcih>lcne chlorideI't'lrilL'llltHDClllCIlL
I.I.2J- IciruchliihKiluin;TolueneTrie hi oroeihc neXykne (lolal)
B-IO10-11-41 5y/ 17/9641 25IH9A
< 10 U< 10 U
10 U10 U10 1!10 U10 1110 U10 U10 U
B-llI l l - l 59/17/96
125UI9A
< 52 U< 52 U* 52 II< 52 1)<: 52 U
28 1< 52 U< 52 U< 52 U< 52 II
B-II118-9
9/17/968 5
UIOA
< 10 U< 10 U
10 U< 10 I)< 10 U
10 II
- 10 U< 10 U< 10 II
10 II
B-llI l l l - l l 59/17/90
1125BI9A
< 10 U< 10 [1< 10 II< 10 U< 10 II<• 1 11 II
10 (I< 10 U< 10 U< 10 11
B-M1 1 2 0 5 - 2 19/17/962075BI9A
< \Q U< 10 II
10 U- 10 II
- 10 II
< 10 II
< 10 II< 10 U< 10 (I< 10 11
aCD
S/2IW TABLE! XLS PigeSof 16
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NATIONAL PRESTO INDUSTRIES, INC.EAU CLAIRE, WISCONSIN
TABLE 3
Summary of VOCs Delecled in Soil Samples - 1996
TAKGtt COMI'uUND(units in ut"k^)
SITE:SAMPLE ID:DATbCOLLfcCILD.AVLRAGi; DEPTH (ft)SAMPLE DKLIVI-RY GROUP
Aceione2-BiH;inonel.l-DichluroahaiH1
1.1 -Dichloroeltiem-Meth>lene chloriderttrachinruellieiif
I,l.2.2-Tclrad)lo(,n.'ilijncI'nliiencrrichloroetheneXylciic (lolal)
[1-11im-il.59/i7/y&31 25HI MA
< 10 U10 II1 (1 1110 11
< 10 U10 U
< 10 U* 10 U
10 U
10 II
B-MII4I--1I 5
9/17/9641 25I1I9A
< 10 U< 10 (I< 10 II< 10 U< 10 U< 10 U< 10 U< 10 U< 10 II< 10 II
B-ll11495-509/17/964 9 7 5
BI9A
< II U< II U
II IIII 1)
< II U< II U< 11 U< 1) [J< II II< II U
B-I2AI2AI-I 59/2 J/%
1 25014
< 53 U< 53 U< 5.) II< 53 1)< 53 U
12 J< 53 It< 53 U< 53 II
< 53 II
B-I2AI2A6-659/23/96
6 2 5nn
< 10 U< 10 Uv Ml II
10 I /
< 10 II
10 U10 II
< 10 II
10 (1
10 II
0)a0)— i0)
S/21/97 TABLE] XI.S Plgebof 160
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TABU: 3
Summary of VOCs Detected in Soil Samples - 1996
TAKtibT COMPOUND(units in iir/'kg)
SITE:SAMPLE ID.DATtCOI.U-XTH)AVhRAGIf DEPTH (ft).SAMPLE DELIVERY GROUP
Acetone2-Buianonc1,1-DiuhIoroeihaiKl,l-[)ichloroelhcitL
Melhylcne chloruli1
J'ciradilimiL-lliL'iiiI.I,2.2-Tciradili>riiL'ilianeToluenerrichloruetheneXylcnc (total)
B-141455-6y/i y/%
5 7 5[114
< 10 U< 10 U
10 (110 II10 II10 II
10 U10 010 U10 U
B-141413 5-1-1y/iy/%
1 3 7 5BU
< 10 U< 10 H
10 U< 10 (1* 10 II
< 10 H
< 10 H< 10 (I< 10 I)< 10 I)
B-1414205-219/|y/y620.751)14
< II U< II (I< II II
II IIII 11
< 11 U< II U< 11 II< II U< 11 U
B-141430-31 59/1 y/%3075UN
< 11 U< II U< II U< II II< II U< 11 U< II i)< n u< u 0< n u
B-I5AISAM 5W23/96
1 25BI4
< 52 U< 52 U< 52 [J
52 11< 52 II
12 J< 52 I)< 52 11< 52 II< 52 U
Pigc^of 16
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NATIONAL PRESTO INDUSTRIES, INC'HAU CLAIRE, WISCONSIN
TABLH 3
Summary of VOCs Detected in Soil Samples - 1996
lAROhl COMCOUND(units in ng'k^)
SITE:SAMPLE ID:IMlfcCOI.LL-CIHJAVERAGE DEPTH (ft).SAMPLE DELIVERY GROUP
Acetone2-Rula<K)neI.l-Dichloruetharii:l,l-t)k)iliimelhciiL'Methylenc chlorideI'e (rath lorocl hen L-1,1,2,2-TelrachloruclhaneTolueneIrichloruetheiieXylcnc (loial)
B-I5AI5A6-6.59/2J/96
625D14
< 10 U< HI I)
10 I)10 1)10 [ I
10 U- 10 II< 10 U
10 U
10 II
B-15AI 5 A I 0 5 - 1 I
y/2j/%1075014
< 10 U< to it< 10 (1
< 10 (1
< JO I)< 10 II< 10 U< 10 (1< 10 (I
10 U
B-15A15A20-2Iy/2.(/i'b
205fill
< 10 U< 10 [1
10 U10 I)
< 10 U< 10 II
< ID i;10 11
< 10 U10 II
B-I5A15A3IO1 5
9/2J/V631 25H14
< 10 U< 10 U< 10 (1
< 10 11< 10 (I
< 10 II< 10 U< 10 U
< 10 U10 II
B-16
161 1 5
9/2 J/%1 251)16
< !l U< 11 U< M II< II II< II H
4 JII 11
< II I)< II 11
II 1 1
CDa0
Page 10 of 10CD
NATIONAL PRESTO INDUSTRIES, INC.I-AU CLAIRE, WISCONSIN
TAI3LL3
Summary of VOCs Detected in Soil Samples - 1996
TAKGLTCUMrolJNU(units in ufk^)
SITE:SAMPLE ID:l)AM-:COI.I,bCII.I>AVL.RAGI: DEPTH (It)SAMPI.liDHl.lVI RYCiKOUl'
Acelone2-Buianone1 . l-DiLliloroelhiiiii.-IJ-Didiliimelhan:v)elh>k»e thloriifi1
I'etrajhlorocltu'iiL-I.I .2.2- lciriidiluiin.-ili.ineToluenerricnlomcilicneXylcnc (loial)
B-161 6 7 5 - 8 5y/23/<;6
8
1116
10 U
10 U10 11
to u10 11
1510 U10 11Ml U
10 II
B-161 6 1 1 - 1 1 59/2 3 /y 6
0
DI6
< 10 U< 10 U
< 10 (1< 10 11
2 J< 10 U< 10 UY< 10 II
< 10 II
10 II
B-161620-205y/2-t/'t&2025im
< 10 U< 10 II
10 11
< 10 It10 It10 U10 U10 U10 II
10 II
B-1616305-31 5
y/24/%30.7?
1113
< 10 U< 10 II
< 10 II
< 10 II
3 J< 10 II< 10 UY< 10 11< 10 II< 10 II
B-16164 1 --4 1 59/24/'J6
41 25B13
< 10 U[0 II
10 (I
10 II10 U
10 II10 II
10 1 110 1110 II
Pl|c II of Id
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NATIONAL PRESTO INDUSTRIES, INC.EAU CLAIRE, WISCONSIN
TABLE 3
Summary of VOCs Detected in Soil Samples - 1996
1 TARGET COMPOUND(units in ug.'kg)
SITE:SAMPLE ID:DATE COLLECTED.AVERAGE DEPTH (ft):SAMPLE DELIVERY GROUP:
Acetone2-BulanoneI.l-Dichloroelhaiu:I.l-DichloroelhcncMethyl cne chloride1 L'lnictilfiroclhciiL1 , 1 ,2,2-'l"i:trai;hluriioiliiineToluenerrichloroetheneXylenc (total)
B-17I 7 S - I
9/24/96075III.!
< M U< II I)
II II< II U< II U
II U< II U< 11 U< 11 U
11 11
B-171 76-6 59/2-1/96
625HI3
< 10 U< 10 II< 10 II< 10 U< 10 II
< 10 II
< 10 U< 10 U< 10 U< 10 If
0-171 7 1 0 5 - 1 19/24/96
10751113
< 10 U< 10 U
10 II
< 10 U2 J10 1)
< 10 UY< 10 U< 10 II< 10 U
B-171720.5-219/24/962075
1113
< 11 U< II U< II (I< II U
3 J< II 1)< 11 UY< 11 U< tl U< II U
B-1717305 -31 5
9/24/9631
HH
< 10 U< 10 II
< 10 II
< 10 U2 J10 U
< 10 UY< 10 U< 10 II< 10 U
Stfl/97 TABLEJXLS 12 of 16
CDaCD-i0)C/>wonQ)'r-t-
CDw
NATIONAL PRESTO INDUSTRIES, INC.L:AU CLAIRE, WISCONSIN
TABU; 3
Summary of VOCs Detected in Soil Samples - 1996
TARGE 1 COMI'uUND(uniis in up kg)
SITE:SAMPLE 10DAlHCOI.LLCiliUAVERAGE DEPTH (ft)SAMPLE DELIVERY (SROdl'
Acetone2-BuianoneI.I-DichloroelhaiiuI.l-DichloroelhencVfelhykne clilorukretrachloroetherik.1
1 , 1 .2,2-Tetrachlon>i;iliiineTolueneIrichtoroclhcneXylcnc (imal)
B-18BI8H5-Iy/2-i/%
0 7 51)1. t
< 52 U-- 52 U•; 52 U
52 1152 U12 J52 U52 U52 I)12 J
R-ISR18118-859/2 4/%
8 2 5BI4
< 10 U< 10 [I< 10 U< 10 U< 10 U< 10 U< 10 U< 10 U< 10 U< II) tJ
B-18BI8UI05-I2
y/2-1/%M 25IJI4
< 10 U< 10 U< 10 U
10 U10 U
< 10 U< 10 I!< 10 U< 10 If
10 U
B-ISBI8B205-2I
9/24/9b2075BI3
< 11 U< II U< II U< n u< II II< 11 II< II 11< 11 11< II II< II II
B-I8BI8B31-3I 5
y/24/%31 25BI3
< II U< 11 II< II U< 11 U< II II< II II< It II< It I I< II U
II 1 1
(I)aCD-iCDWW0o
VII/97TABLEJ XLS Pigt Uof 16CDM
NATIONAL PRESTO INDUSTRIES, INC.EAU CLAIRE, WISCONSIN
TABLE 3
Summary of VOCs Detected in Soil Samples - 1996
IAKGLT COMPOUND(units in u^/k^l
SITE:SAMPLE II>IMIfcCOI.UCTIil)AVERAGE DEPTH (ft).SAMPLE DEI.IVI-:RY GROUP:
AcetoneJ-BulanoneU-Dichloroelhanc'.l-nidiloroelheiiLMelhylciie ^Jiloriili.'
clrachlorocihene,l,2,2-Telrai;hliiriii:(li;ine
1 ol ucncIricJiloroclhent:
Xylciif (total)
B-I9A1 'MO 5-1 5
y/ 17/961
BI9A
< 52 U52 U52 II52 U52 U
42 J52 U52 U52 V
52 II
B-I9AI9A6-659/17/96
625UI9A
< 10 U< 10 I)< 10 11< 10 II
< 10 U< 10 II
< 10 U
< 10 11
< 10 (I
< Id II
B-19A
19AH-II.5
9/1 7/%IE 25UI9A
< 10 U< 10 U< It) 11
10 I)
< 10 U< 10 U< 10 11
10 U< 10 II< 10 II
B-19A
I9A2I-2I 59/17/9621 25BI9A
< 10 U< 10 U- 10 li< 10 U< 10 U* 10 II•; ID n< 10 11< 10 11
< 11) II
B-I9A|yA3l-3l 5
9/17/46
31 25BI9A
< 10 U10 II10 II
10 II< 10 I)
10 IIII) (I
< 10 tl< 10 U
III U
0)aCD-i0)Cflw0o
Pigc MoTI6
NA IIONAI, I'RI-STO INDUSTRIES, INCI-:AU CLAIRE, WISCONSIN
Summary of VOCs Detected in Soil Samples - 1996
IAKGL1 COMI'ulINU(units in ti^'k^}
SITE:SAMPLE ID.DAILCOI.I.RTU)
AVERAGE DEPTH (ft)1
SAMP1 1: Dill IVI KYfiKOlU'
Acetone2-llul;iiinMcI.l-DklilomclhiimIJ-Didiloroclheik:Ucthylciu: dilnruiu
rctradiluroclhiiiK1
1 1,2 2- I'clradilimn ili.incTolucnt1'rictiloroclhene
\>lctii: (lolal)
B-20
2(12-3 5>>/ 1 7 /Mb
2 2 5ni^A170
M 11
55 U
53 II
51 11Mil
5.1 II5) U
53 II51 (I
B-20205 5-6 5
y/17/%6
U19A
< 10 LI10 U
< 10 II
< 1 (1 1 1< 10 11
< 10 (1< 10 II
- 10 II
< 10 II<- 10 II
B-202(112 5-13
M/I7/V6
12 75HI'M
< 10 U10 U10 11
10 U< 10 II
10 IIId II10 U10 [110 II
B-2020205-21
y/17/%20.75BI<M
< 10 U
< 10 (I< 10 II
< 10 II
< 10 II
< 10 U< 10 (1
< 10 II< 10 U
10 1 1
B-20
20.10-30 5l)i 1 7/%
3 0 2 5
um- 10 U
10 11
10 U
- 10 11
10 U< 10 tl
10 H
10 II
< 10 II
- 10 II
(Da0)—iD)W(/)Oo
S/2I/V7 TABLE! XI S P*ge I
NATIONAI PRESTO INDUSTRIES, INC.[EAl CLAIRE, WISCONSIN
TABU: .3
Summary of VOCs Detecled in Soil Samples - 1996
TARGET COMPOUND(units in ug/kg)
SITE:SAMPLE ID:DA IE COLLECTEDAVERAGE DEPTH (ft):
SAMPLE DELIVERY GROUP
Acetone2-nuianone1,1-Dichloroelhane1,1-Dichloroelhene
Methylene chloridelelrijchloroclhcrii-
1.1.2.2-l'clructilimiclhanclolueneffichloroetheneXylcnc (total)
G-l(i-1
y; 2 4/%0 2 51113
< 26 U2ft U26 U
< 26 U
1 J
:t> ii2b liY
< 2ft U< 26 II
2d U
G-2G-2
9/24/y60 2 5KM
< S3 U< 53 U< 53 U< 53 U
16 J21 J
< 53 MY< 53 I)< 53 U< 53 11
NPILISS-ANP1I.1SS A
'>/-)/%025Ni>l
153 J
< 1(1 1)< 10 II< 10 (I
< III U/
< 10 |l/
< 10 HZ
< 10 II< 10 |l/
NPILISS-B
NPILISSB4/4/96
0.25
NPI
8 J2 J
< 10 U< 10 U< 10 II
< 10 U/
< 10 HZ< 10 UZ
< 10 U< 10 U/
0atoW(00o
S/2l/y7TABLE) XLS Ptgc Ibof l6
NATION XL PRESTO I N D t STRIKS
EAU CLAIRE, \\ ISCONSIN
TABLE 4
eder associates
PGC ANAL\ TICAL RESI LTS FOR SOIL VAPOR KXHAI ST SAMPLES
Sample l.f). :
B-8 l-l 5
B-8 6-6 5
B-8 1 0 5 - 1 1
B-8 21-21 5
B-8 2 1 5-22
B-8 3 1-31 5
B-8 41-11 5
B-8 5 1-51 5
Sample Dale:
09/18/96
09/18/96
09/18/96
09/18/96
09/18/96
09/18/96
09/18/96
09/18/96
l.l.l-TCA
ND
4 136
1 496
ND
ND
ND
ND
ND
TCE
0057
046
0 301
0027
ND
0 126
0.234
0231
PCE
0066
0428
0 194
ND
ND
ND
ND
ND
TotaMOCs i
4 3 1 6
10421
4244
0.418
1 358
0 547
! 856
0705
Sample l.D. :
0 - 9 0 5 - 1
B-9 6-6 5
B-9 1 l-l | 5
B-9 20 5-21
B-9 21 5-22
B-9 30. 5-3 1
B-9 4 Ml 5
B-9 5 1-51 5
Sample Date:
f W IS/96
09/18/96
09/18/96
09/18/96
09/ 1 8/96
09/18/96
09/18/96
09/18/96
l.l.l-TCA
ND
6.565
ND
2
ND
1.53
ND
ND
RE
0 112
0 1 14
ND
0048
ND
0.068
0.059
0089
PCE
0 107
0369
0.034
0 148
ND
0 126
ND
ND
Total \(H\
1 5 950 i
8 189
1 903
3.428
1 238
8.673
3.673
3 545
Sample l.D. :
li-H) l-l 5
;;-H> iwi 't f - lu in 5-i 1
B-IM 1 1 Ml
B-10205-2 !
B- 10 30 5-3!
B-I04I 5-42
Sample Date:
U9/|4 ^h
ng'io <J(,
09/19 <J^
i W 1 9 96
09/IQ-96
09/19/96
09/19/96
l.l.l-TCA
ND
ND
N'D
ND
ND
ND
ND
TCE
SD
SD
0 0 1 8
002
0.019
0027
0.026
PCE
<Mi22
ND
ND
N'D
ND
ND
ND
f Total \ (K \ !
II 39S
M5" !
[ 01)3
5 004
! 485
0.898
5.233
NOTESND - Not Detected
Total VOCs «ere estimated in ppmv TCE equivalent.
Tin: di::.-.:!'1" ' • " i i : -- : ""' ;i\^ : • \'C \ :' ,-nh .. .- i
Ml L i ) i K ^ : i [ r L i [ [ i ' t ; - > ,irc n: ppm
OS/111" M HYDRO PROJECTS :'4CK.'S\4<)7-TOT WB: Ofl
NATION \L PRESTO IND1 STRIES
EAt1 CLAIRE. WISCONSIN
TABLE 4
eder associates
PGC ANALYTICAL RESl'LTS FOR SOIL V.VPOR E X I I . V l ST SAMPLES
Sample I.D. :
IM1 1-1 5
B-ll 75-8
B-ll I0.5-II
B-ll 21-21.5
B-ll 30.5-31
B-ll 31 5-32
B-ll 405-41
B-n 44-495
Sample Date:
r 09/19/9609/ 1 9/96
09/19/96
09/19/96
09/19/96
09/19/96
09/19/96
09/19/96
i.u-TCA2.86
ND
ND
ND
ND
ND
ND
ND
TCE
0033
0 038
0 06 1
0 128
0.112
0083
0096
ND
PCE
a 23ND
ND
ND
ND
ND
ND
ND
Total \ f>(,
4350
1 528
3070
2.350
1 688
2.424
1.490
1 447
Sample 1.0. : ! Sample Dale:
B- I2A 1-1 5
B-I2A 5 5-6
B-12A 1 0 5 - 1 1
B-I2A 205-21
B-12A3I-3! 5
B-I2A33-33.5
09/23/96
09/23/96
09/23/96
09/23/96
09/23/96
09/23/96
u.i-rr\ND
ND
ND
ND
ND
ND
ITENDND
ND
ND
ND
ND
PCE
0 076
ND
ND
ND
ND
ND
Total \ Of*
2 7 1 9
0638
0366
0337
0251
0981
Sample I.D. :
B-13 l-l 5
B-1365 - ^
H-13 M- l l 5
H-I - :—-:iIM.— 1 - - 1 5B-13 4iM() 5
B-13 41-41 5
Sample Date:
09/23/96
09/23/96
<>9'23'9h
iig, 2V^
f|9/23.'%
D9/23/96
09/23/96
1.1.1 -TCA
23.63
1053
ND
NDND
4240
ND
rcE0 123
ND
PCE
0258
0044
ND | ND
ND
ND
ND
ND
ND
"018
0015
002!
Total VOC- !
27 565 i
1 3 584 !
1 349
: 457; 089
5630 i
3 020 !
Sample I.D, :
B- 14 05-1
B- 14 6-6 5
B-14 13-13 5
n - i 4 :•- : : ;
I!-U .- • ;-M
Sample Date:
09/19/96
09/19/96
09/19/96
' (0 1<) Of ,
'!'«. 14 ')')
I.LI-TCA
ND
ND
ND
NO
ND
TCE
ND
ND
ND
\n\o
PCE
0 123
0018
ND
ND
ND
Total VOr»
1.042
2.973
2.323
<
1 107
NOTES
N D - N o l Detected
Tulal VOC> wire estimated m ppmv TCG equivalent.
The deieclion l imi t is 1000 ppb tor TCA. 45 ppb tor TCE and 35 pph tor PCE
All concentrations are in ppm.
M 'HYDRO PROJECTS G4001S1'J"7.TOT W9-
NATION \L I'KEMO IND1 MUICS
EAi; CLAIRE. WISCONSIN
TABLE -»
eder associates
PGC A N V L \ TIC VL RESI L TS FOR SOIL V VPOR EXIlAl'ST SAMPLES
Sample I.D. :
B-I5A l-l 5
B - I 5 A 5 5 - 6
B-I5A 1 1 - 1 1 5
B- I5A21-21 5
B-15A jO-305
B-15A 3 0 5 - 3 1
Sample l);ire:
09/23/96
09/23/96
119/23/96
09/23/96
09/23/96
09/23/96
I.I.I-TCV
ND
_> 40-4
ND
ND
2.737
2.407
TCE
0030
ND
ND
ND
ND
ND
PCE
1)080
0 058
ND
ND
0.032
0033
rotai vors2.546
3 680
(1882
1.305
2.955
2.746
Sample I.D. :
B-16 0 5 - 1
B-16 6-6 5
H-16 !n 5- II
B- 16 20 5-2 1
B-I621-2I 5
B- 16 30-30 5 '
B- 1640 5-41
Sample l);ire:
09/24/9'--
1)0/2 4. .'9 A
H9/24/96
1)9/24/96
W/24/96
09/24/96
09/24/96
I.I.I-ITV
ND
ND
in 68
:s i?2 762
4 MO
ND
FCE\D
ND
ND
ND
ND
ND
ND
PCE
ND
ND
0 069
ND
ND
0.029
ND
Total VO(\
0889
> 974
11 518
5 170
5000
5 130
0.838
Sample I.D. :
B-17 l-l 5
B - 1 7 5 5 - 6
B-17 M - l l 5
B-1" 21-21 -
B-r -n--.il 5
Sample Dale:
1)9/24/96
09/24/96
(19/24. 9f,
iiQ'24'Oi,
in) 24. '><•
l.l.I-TCA
3408
2067
"227
! S^R
• 2')i
TCE
ND
ND
ND
ND
NO
PCE
0038
0075
0 027
(H)|7
r i r i 42
Total VOCs
6435
4 0 1 1
I O J 3 7
• 649 ;
——————————— ————
Sample I. D. : 1 Sample l);ite: l.l.l-TCA
B-I8B l-l 5
B - I 8 B 7 5 - 8
B-I8B II- l l 5
B-I8B2I-2I 5
B-lgB 3 0 5 - 3 1
G-l
09/24/96
09/24/96
09/24/96
09/24/96
09/24/96
09/24/96
ND
ND
1 721
3.616
ND
ND
t i-2 ! i^ :i 'i- •-:
TCE
ND
ND
ND
ND
ND
ND
PCE | Total VOCs
0044
0.040
0010
ND
oon0040
1 -1
4602
1.921
5348
9245
4380
0957
I'T.
NOTESND - Not Detected
Total VOCs were estimated in ppmv fCE i r q u i ^ a f t n t
The detection l i m i t is 1000 ppb lor I'CA. 45 ppb for TCE and 35 ppb tor PCE
All concentrations are in ppm.
OS/I 1/97 M 'HYDRO PROJECTS'.OJWS 497-TOT WB2
NATION \1. PRESTO I N D l STRIES
EAU CLAIRE, WISCONSIN
TABLE 4
eder associates
PGC ANALYTICAL RESl LTS FOR SOIL \ APOR E X I I A l ST SAMPLES
Sample I.D. :
B-I9A 1 5-2
B-I9A 5 5-6
B-19A in 5 - 1 1
B- I9A20.5-21
B-I9A 2 1.5-22
B-19A305-3!
Sample Date: l.U-TCA
09/ 1 7/96
09/ 17/96
09/17/96
09/17/96
09/17/96
09/17/96
I 701
ND
ND
ND
ND
ND
TCE
ND
ND
ND
ND
ND
ND
PCE | Toial VOCs
0084
ND
ND
ND
ND
ND
2.944
1.190
0 181
0475
1.803
0266
Sample I.D. :
B-20 2.5-3
B-20 65-7
Sample Date: 1 l.l.l-TCl
09/ 1 7/96
09/17/96
B-20 12-12.5 I 09/17/%
B-20 2 1 - 2 1 5
B-20 30 5-31
09/17/96
09/17/96
ND
ND
2.328ND
ND
TCE PCE | Total VOCs
ND
ND
0.324
0025
ND 0156
NDND
ND
ND
5 199
4 8 2 8
9510
2.122! 638
NOTESND - Not Detected
Total VOCs were estimated in ppmv TCE equivalent.
The detection l imi t is 1000 ppb lor TCA. 45 ppb for TCE and 35 ppb tor PCE
All concentrations are in ppm.
05/21/97 M HYDRO' PROJECTS' OJOO'S',4<>7-TOT WB2
eder associates
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NATIONAL PRESTO INDUSTRIES, INC. —•EAU CLAIRE, WISCONSIN
TABLE 6
Summary of SVOCs Detected in Soil Samples - 1995
fAKCEltOMI'OUNO(units in n^ Kg)
SITE:SAMJ'I.K ID:hAlttOl.I.tC IKI):AVERAGE DEPTH (H):SAMPI -E DEMVKKY (;KOlJP:
Di-n-bulyl phlhuhikI'hcriiinthrcnc[lll[>l foeil/)! pl l t l l . l l .UC
t 'cntachlnroplKinil2-Mctli)lnaph!liali.-[n.His(2'flli>lliL-\yl) plnli.ilulcl)i-n-tiLl)l pliOuibk'>(i;in;•luoramlicnc
riir>scrii;
It 01U 1 2JIJ8/JO/95
23111 II
14003: Mi u•>2 J840 UY3 SO II,M) J
350 U350 II35(1 (1350 I/
B-OI11 1 25M/JU/VS
25B 1 10
850< 350 II
350 II< 840 UY
ISO II
- 350 II< 350 11< ,1 SO II< 350 U< 350 II
BOIB-l-278/JO/9S
2711 1 Ml
160 J< 150 U
350 II850 1)150 II350 U350 U350 II150 U
- 350 11
BO]B 1 298/3(1/95
2911 1 Ml
560< 350 [J< 350 (I< 850 U
350 II< 350 II
350 II35(1 II350 II
< 350 IS
B-OI11-1-338/3«/ys
33It-1 10
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TAIJLl. 6
Summitry of SVOCs Detected in Soil Samples - 1995
IAK(,KI < OMHH.Nl)
(units in UK'^K,)
SITE:SAMPLE ID:DATE COLLECTED:AVERAGE DEPTH (ft):SAMPLE DEI.IVEKY OKOIH':
Di-n-buiyl phlhal.it>1 'he nan ill re DCHulyl hcii/yl phlli.ii.it.
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TABLE 6
Summary of SVOCs Detected in Soil Samples - 1995
IARGEI (OMI'OI'M)(units in u^'kg)
SITE:SAMPLE ID:!>A IK< Ol 1 H IH>;
AVERAGE DEPTH (fl):SAMPLE DELIVERY GROUP:
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B-07n 7 ion8/31/M
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NATIONAL PRESTO INDUSTRIES, INC.EAU CLAIRE, WISCONSIN
TABL1-6
Summary of SVOCs Detected in Soil Samples - 1995
1 MUitl COMPOUND(units in ug/kg)
SITE:SAMPI.tll>:l><Ut<OI 1 tl IHl;WKKAGt; OKI' III (ft):SXMI'I K I)H IVFKV GROUP:
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TABLE 8
Summary of PCBs Detected in Soil Samples - 1995
TARGET COMPOUND(units in iiE'kn)
SITE:SAMPLE ID:DATE COLLECTED:AVERAGE DEPTH (ft):SAMPLE DELIVERY GROUP:
Aroclor-1254
B-OIH I 3 1
8/31/9531
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< 35 U
B-02
B-2-0
8/30/950
It 1 III
< 3400 II
B-02
B-2-5
8/30/955
11 1 10
< 37 U
B-02B-2-10
8/30/V510
B 1 10
< 3600 1 1
B-02
B - 2 - I O D
8/30/9510
II 1 Ml
3500 U
S/2I«T TABLEIX1.S
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NATIONAL PRESTO INDUSTRIES, INCEAl CLAIRE, WISCONSIN
TABLE 8
Summary of PCBs Detected in Soil Samples - 1995
TARGET COMPOUND(units in uj;/kg)
Aroclor-1254
SITE:SAMPLE ID:
DATE COLLECTED:AVERAGE DEP III (ft):SAMPLE DEI.IVI RY GROUP:
B-04
B4 15
8/31/9515
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8/JI/9525
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28B-l-0
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NATIONAL PRESTO INDUSTRIES, INC.EAU CLAIRE, WISCONSIN
TABU: 8
Summary of PCBs Detected in Soil Samples - 1995
TARGET COMPOUND(units in ug/lte)
SITE:SAMPLE ID:
DATE COLLECTED:
AVERAGE DEFMI (ft):SAMPLE DEI I V K R Y GROUP:
Aroclor-1254
B-04
B-4-308/31/95
30B I O
< 35 U
B-04B-4-32
8/31/9532
B 1-0
< 34 II
B-04B4 348/3I/9S
3411-4-34
< 3500 U
B-04B-4-368/31/95
36B I D
< 34 U
B-05B-5-2
8/31/952
B 1 10< 34 11
CDaCD
J/JI /97 TABLEIXLS I of II
NATIONAL PRESTO INDUSTRIES, INC.EAU CLAIRE, WISCONSIN
TABLE 8
Summary of PCBs Detected in Soil Samples - 1995
TARGET COMPOUND(units in i i£/l>K)
SITE:SAMPLE ID:DATE COLLECTED:AVERAGE DEPTH (R):SAMPLE DEI . I V E R V (.ItOU1:
Aroclor-1254
B-05
B-5-2RE
8/31/95
2
H I 1 0
< 34 U
B-OS
B-57
8/J1/957
1) 1 0
< 34 V
B-05B-5-7
8/31/957
B 1-0
< 3300 U
B-05B-5-128/31/95
12H I H I
< 34 U
B-05
B-5-168/31/95
16
B 1 10
< 36 U
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NATIONAL PRESTO INDUSTRIES, INCEAU CLAIRE, WISCONSIN
TABLE 8
Summary of PCBs Detected in Soil Samples - 1995
TARGET COMPOUND
(uni t s in uji/^K)
SITE:SAMPLE II):
DATE COLLECTED:
AVERAGE DEPTH (ft):SAMPLE DELIVERY GROUP:
Aroclor-1254
B-07
B-7-58/31/95
5U 1 If
332 J
B-07B-7-10
8/31/9510
B-l-0
< 34 U
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8/31/95
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S/21/97 TABLE! XLS 11 of 11
NATIONAL PRESTO INDUSTRIES, INC.EAU CLAIRE, WISCONSIN
TABLE 9
Summary of PCBs Detected in Soil Samples - 1996
TARGET COMPOUND
(units in ug/kg)
SITE:
SAMPLE ID:
DATE COLLECTED:
A V E R A G E DEPTH (ft):
SAMPLE DELIVERY GROUP:
Aroclor-1242
Aroclor- 125-1
R-08
8.5 1
9/19/96
0.75
B8
3600 U
< 3600 U
B O H
86.5-7
9/19/96
6.75
B8
< 1700 11
< 1700 U
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811 12
9/19/96
11.5
BS
< 35 U
35 U
B-09
91 -1.5
9/19/96
1.25
B8
< 3300 U
< 3300 (J
B-09
95.5-6
9/19/96
5.75
B8
< 3300 (1
3300 [1
VI1/97 TABLES XLS Ptgc 1 of 12
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NATIONAL PRESTO INDUSTRIES, INC.EAU CLAIRE, WISCONSIN
TABLE 9
Summary of PCBs Detected in Soil Samples - 1996
TARGET COMPOUND
(units in iiji k j - 1
SITE:
SAMPLE ID:
DATE COLLECTED:
AVERAGE DEPTH (fl):
SAM I'LL UEMVEHV GROUP:
Aroclor-1242
Amdt . f -1254
B-12A
12AJ0.5-32.5
9/23/96
JUS
BI2A21
14 UN
3-1 nil
B-I3
131 1.5
9/24/96
1.25
BIJ
< 3-10(1 I)
3-100 1 1
B-13
136 6.5
9/24/96
6.25
BIJ
641) U
d'W U
B-13
1 3 1 0 5 I I
9/24/96
10.75
BIJ
< 3-1 II
< 34 11
B 14
1 4 1 - 1 . 5
9/19/96
1.25
BI4
< 34(10 I)
34UO U
(DaCD"iD)COWoo
S/2J/97TABI.E9XLS
NATIONAL PRESTO INDUSTRIES, INCEAU CLAIRE, WISCONSIN
Summary of PCBs Detected in Soil Samples - 1996
TARGET COMI'OUND
(units in u^ 1,^)
SITE:
SV MI'1 KID:
DATE COLLECTED:
AVtRACE DKI'llllfll
SAMPLE DU.IVKKl (;KOHP:
Aroclor-1242
Arudi>r-125-l
B 14
145.56
9/19/96
5.75
IH 4
< 350 U
.150 U
B-I4
I 4 I J 5 M
9/19/96
IJ.75
UN
< 35 U
< 35 U
B-15A
1SAI 1.5
9/19/96
1.25
HI4
< 340(1 U
3-11)0 (1
B-I5A
1546-6.5
9/19/96
6.25
BI4
< 3500 ' U
•; 3500 II
B-15A
I5.UU.5-M
9/19/96
Ml. 75
HI -I
< 35 U
35 H
0)aCD-i[D
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S/2I/97TABLE9XLS P*«6oM2CD
NATIONAL PRESTO INDUSTRIES, INC.EAU CLAIRE, WISCONSIN
TABLE 9
Summary of PCBs Detected in Soil Samples - 1996
TARGET COMPOUND
(units in u^/kg)
SITE:
SAMPLE II):
DATE COLLECTED:
AVERAGE DEPTH (ft):
SAMPLE DELIVERY CROUP:
Aroclor-1242
Aroclur-1254
B-16
161-1.5
9/24/96
1.25
B16
3600 11
36(10 U
B-16
167.5-8.5
9/24/96
8
BI6
< 1700 U
< 1700 11
11 16
1611 11.5
9/24/96
11.25
UK,
< is u
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17.5 1
9/24/96
0.75
BIJ
< 36 U
36 U
11-17
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9/24/96
6.25
BI3
< 34 U
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NATIONAL PRESTO INDUSTRIES, INC.EAU CLAIRE, WISCONSIN
TABLE 9
Summary of PCBs Detected in Soil Samples - 1996
TAH1.KT COMPOUND
(units in ug/kg)
SITE:
.SAMI'I K I D :
UATtCOl I.KCTKO:
\ \KKA(,K DH'III (II):
KAMI'1 K III ll\ 1 U\ <.KO|iP:
Arocloi I 242
Aimlni I J _ S 4
B-20
2012.5-13
9/17/96
12.75
BI9A
< 34 U
34 1)
B-20
2012.5-IJKt:
9/17/96
12.75
BI9A
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TABLE 9
Summary of PCBs Detected in Soil Samples - 1996
TARGET COMPOUND
(units in UK/kit)
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TABLE 1U
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lAtU.LI COMPOUND
(units in inn 'kg)
SITE:SAMPLE ID:DATECOI.l.ta IU>:AVERAGE DEPTH (ft}:SAMPI K DKI.JVI HY CKOUP:
AluminumAntimonyArsenictar iu in)er> Ilium
Cadmium1 'akiimiChromium
CobaltI 'upperCyanide
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B-OIB-1-23I>8/30/95
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TABLE 10
Summary of Metals Detected in Soil Samples - 1995 Data
TARGET COMI'ODNL)(units in in^/kg)
SITE:SAMPLE ID:UATECOLLttmi:AVERAGE DEPTH (ft):SAMPLE DELIVERY GROUP:
AluminumAntimonyArsenicJariumtcr> Ilium
CiiiJiiiiuniCalciumCnnmiiumCo ball
CopperCyaniderun
.cadMagnesiumManganeseVlacuryNickelI'otabsiumSeleniumSodiumVanadiumZinc
B-03B-3-7U8/31/95
7
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8/31/959
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B-03B-J-IJ8/31/95
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TABLE 1U
Summitry of Melals Detetled in Soil Samples - 1995 Data
TAKGti nmroiiNi)(units in tun kg)
SITE:SAMPLE II);DAItCOI.l.tC IKD:AVtHAGK DEPTH (ft):SAMPLE DM IUK\ GHOIU':
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leadMagnesiumManganeseV1eicur>Niekdi'liLiSMimiSeleniumSodiumVanadium^inc
B-03B-3-17
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B-4-34
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TAIiLL 10
Summary of Metals Detected in Soil Samples - 1995 Data
TARGET COMPOUND
(units in rn^'kg)
SITE:SAMPLE ID:OAlfcCOU.fcOKl);AVERAGE DEPTH (ft):SAMI'l t l»i:i H Kin GKOUP:
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TABLE I ]
SUMMARY 01- METALS DETECTED IN SOIL SAMPLES - 1996 DATA
SITE:SAMPLE ID:
TARGET COMPOUND DATE COLLECTED:
(units in m^/kg) AVERAGE DEPTH (ft):SAMPLE DEI. l\ KIU <,K<H (':
AluminumAntimony
Ann: me
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Copper
Cyanide
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< 062 II
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TABLE 11
SUMMARY 01- METALS DETECTED IN SOIL SAMPLES - 19% DATA
SITE:SAMPLE ID:
TARGET COMI'OUND DATE COLLECTED:
(units in nit; 'MO AVERAGE DEPTH |ll(:SAMPLE DfcLIVKUY GROUP:
A l u m i n u mA n t i m o n y
Arsenicl u r iun i
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TABLE 1 1
SUMMARY 01- METALS DETECTED IN SOIL SAMPLES - 1996 DATA
SITE:
SAMPLE ID:
TARGET COMPOUND DATE COLLECTED:
(units in nig/kg) AVERAGE DEPTH (It):
SAMPLE DELIVERY GROUP:
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Aiiliiiuiny
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TABLE 11
SUMMARY Ol; METALS DETECTED IN SOIL SAMPLES - 1996 DATA
SITE:SAMPLE ID:
TARGET COMI'OUND DATE COLLECTED:
(units in mi;'kg) AVERAGE DEPTH (ft):SAMPLE DELIVEKV GROUP:
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Arsenic
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198 H
< 0.63 U54 5 It
< 13 11
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B-ll1120.5-21
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< 021 111 100
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< 005 U
6 1 It
190 It
< 062 U
474 B< 12 U
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707
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213 B
< 061 11
53 It
< 1 2 11
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186 It
< 062 II
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S/21/97 TABLE) I XLS 6 of 19
NATIONAL PRESTO INDUSTRIES, INCI-A IJ CLAIRE, WISCONSIN
TABLL II
SUMMARY 01 METALS DETECTED IN SOIL SAMPLES - 1996 DATA
SITU:SAMPLE ll>:
TARGET CO.MI'OUND I>A 1 1 COU.ECI fcl):
( u i i i l s i n m ^ k t f ) AVtIUGh DEPTH <fl) :SAMPLE I)U IV 1 in t.KOM':
AluminumA n l i m n n )
\r icnic1 arm in
['jjnmim( ' jkil l l l l
ChromiumI ' ubu l l
Copper
Cyuniilc
iiiii
.ead
vlagncsium\1iiiigaiiLin;
Vlercury
NickelI 'utas^iumSeleniumSodium
Tha l l iumVanadium/me
U l l
IH!>.5 50
J5327
4'>.7S
Bm782
< 065 U
065 1)
24 II
0 18 HMo n3 1
051 I t23 I t
015 H1010
065
1 50 B
8 5
005 if
37 B157 1)
< 065 11
< 37 1 11
< 13 II
32 I t97
B-I2A
I 2 A I 1 535331
1.25
U N
4210< (K.I 11
1 1 11
22 K It
d - 1
2 l K > 0
K i l l5 1 H
-18 S
•1 2
127(10
21 C>
288»I I K
< 0 (15 I I549
24t> 11< 0 6 1 11
10') 11
< M I I
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0 72 11
14 It
82
1050
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21 3
1 7
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1 81200
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< 0 05 U
126
172 K
< 062 II
635 It
< 1 2 I I
12 5196 1
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NATIONAL PRESTO INDUSTRIES. INCEAU CLAIRE, WISCONSIN
TABLE 11
S U M M A R Y 01- METALS DETECTED IN SOIL SAMPLES - 1996 DATA
SITE:
SAMPLE ID:
TARGET COMI'OLIND DATE COLLECTED:
(units in m- kj;) AM HU.K DEPTH (ft):
SAMPLE DEI IVt:m GROUP:
Aluminum
Anliiiiiiii)
\FMrnk
l^iniini
i 'udniiumCalcium
l 'Imiiuium
Cnbah
Copper
t'y.iiudc
run1 cud
vlagnesium
Miiriganoc
Ucruiry
Nitkd
'nU iiini
Selenium
Sodium
IhiilliiJiii
VanadiumZinc
B-I2A12AJOS-32.5
35331
J1.5
BI4
1620
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< 062 11
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3 S861 1)
II 2
29 D
20 S
041 H*
4 MO
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698
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178 I)
< 062 11
377 II
< 12 (I
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178 1
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-i
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26 M
30 1 ii*
2 (> N
5251)
277
1-150
676
< 005 U
ID 1
146 11
< 062 U
18 H
i : n92 U
286 T
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3 81820 1-
61 5 N
3 5 H
189 n*
1 d N
10800
142
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107
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< 062 U
121 n1 2 II
21 4
177 i;
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353 Jl
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NA
NA
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NA
NA
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NA
NA
NA
NA
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NA
NA
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NA
NA
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TABLE 11
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SITE:
SAMPLE ID:
TARGET COMPOUND I»A IE COl.l-ECI El>:
(limit in m,' KK) AVbKA(;t: I1EH 1 H III):
SAMITE DEI IVEI<\ <;K<l|i|>:
Aluminum
Anliiiiiiny
Arsenic
H.iniim
t'ailmium
L'aluiii]]
Chromium
Cofojli
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CjJ
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Vltingancse
Mercury
Nickel
I'otassiumSelenium
Sodiumthallium
Vanadium/inc
B-14
14135 14
JSJ27
13.75
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3140
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166 11
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< 015 U*
7650
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839
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< 063 U
606 M
< 13 II
178
197 F
B 14
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35327
2)1.75
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202 It
< 065 if
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21 7 I-
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065 U
102 il
21 6
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7 6
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11 4
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108
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1H2
210 B
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NA
NA
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N\
NA
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NA
NA
NA
NA
NA
NA
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NATIONAL PRESTO INDUSTRIES, INC.EAU CLAIRE, WISCONSIN
TABLE 1 1
SUMMARY 01 METALS DETECIED IN SOIL SAMPLES - 1996 DATA
SITE:SAMPLE ID:
TARGET COMPOUND DATE COLLECTED:(uniii in mj> /kg) AVERAGE DEPTH (ft):
SAMPLE D E L I X Kin (.HOUP:
AluminumAntimony
•\riCinc
lit! Ill III
Cadmium
i 'aluum
r i i r i i i n i u i uCohaliCopper
Cyiiindc
Mil l
1 cadVliigneiiumMjnganeicMercuryNickel
I'ofasiiumSeleniumSodiumI h u l l i u n iVanadium£inc
B-16161 1.535332
1.2511 16
2750 •< (1 64 11
1 1)
178 116 1
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1433 1 H2 3 5
1 8
69901 9 4
1570
695 n
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155 U
< 0 64 U
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1 5 2103 •
B-16
167.5-8.535332
H
1116
41)70 *
< 1 2 4 I I1 M
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3 5|79il
56 15 5 li
2 8 h< 21 h
l i ooo3 6
2980
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2 2 8
187 It
< \ II
81 2 tt< 2 1 I I
1 9 53 7 7
B-16167.5-8.5 D
J53328
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3654
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3960
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28 1
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< 062 U
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B-161 6 1 1 11.5
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B-161620-20.5
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NA FIONA , PRESTO INDUSTRIES, INt:EA CLAIRE, WISCONSIN
TABU; 11
SUMMARY ()l METALS DETECTED IN SOIL SAMPLES - 1996 DATA
SITE:VAMIM.EW:
TARGET C'OMI'OUND DA It COI.l.tC 1 tl>:
(unilsin rnjykg) AVLKAGt:i>t:PII«rt>:SAMPLt Utl.n i:H\ <;ROHP:
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•\tSailC
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I'aluuin
ChromiumC'ohali
t'oppLf
("yiimdi:
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lead
Magnesium
V1 ui leanest:
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Si! J] III II
llulliinn
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B 16
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35332
31
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069 1)
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26 li
22 2 n*
< 015 II
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< 0 05 U
1 8 2
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TABLE I I
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SITE:
SAMPLE ID:
TARGET COMI'OUND 1>ATE COLLECTED:
(units in m- ) | AVtU\t;t DEM II (fl):
SAMPLE IIEI IVI.K\ GROUP:
Aluminum
A til iin ixiy
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tannin
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run
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Nickel
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Irnillium
Vanadium
^inc
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11.25
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31 1
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172002
218 11
< 062 U
542 II
< 12 II
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35332
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.1 s it
3-4 -1 ii*
< 016 U
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< [1 64 1 1
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< 11 11
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294 1
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< 016 II
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< 065 If
826 It
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NATIONAL PRESTO INDUSTRIES, INCEAU CLAIRE, WISCONSIN
TAUI.E 1 1
SUMMARY 01- METALS DETECTED IN SOIL SAMPLES - 1996 DATA
SITE:SAMPLE ID:
TARGET COMPOUND DATE COLLECTED:(units In iii^'kg) AVERAGE DEPTH (ll»:
SAMPLE DKIJVKin GROUP:
Aluminum
AmmiiwyArsenic
Barium
ltcr> Ilium
Cadmium
Calcium
Chromium
I'ohall
I 'upper
Cyanideron
leadMagnesium
Manganese
vfcrcuryNickel
I'olassiumSeleniumSilverSodiumThalliumVanadium
/.iiiL
B202030-30.5
9/17/96
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< 021 H
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539 N
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4601 *
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NATIONAL PRESTO INDUSTRIES, INC.EAU CLAIRE, WISCONSIN
TABLE 12
PRELIMINARY CAPITAL COST ESTIMATE fVADOSE ZONE SOIL1ALTERNATIVE V-l - NO FURTHER ACTION
Description
Contaminant Transport Modeling
Backfill Lagoon
Engineering Design
Construction Administration
SUBTOTAL
Contingencies (@ 20%)
TOTAL
Estimated Cost
$ 40,000
$250,000
$ 10,000
$ 5,000
$305,000
$ 61,000
$366,000
NOTES:
Cost estimate does not include operation, maintenance and monitoring costs for the IRAsystem at the southwestern portion of the NPI site (estimated 10 years of operation requiredunder this alternative).Assumes $5/cy to place on-site fill material in lagoon.
U.V59SOWT
eder associates
NATIONAL PRESTO INDUSTRIES, INC.EAU CLAIRE, WISCONSIN
TABLE 13
PRELIMINARY CAPITAL COST ESTIMATE CVADOSE ZONE SOIL!ALTERNATIVE V-2 - SOIL VAPOR EXTRACTION
Description
SVE System InstallationSite WorkEquipmentEquipment BuildingElectrical Controls
SUBTOTAL
Backfill Lagoon
Engineering Design
Construction Administration
SUBTOTAL
[ ,._Contingencies (@ 20%)
TOTAL
Estimated Cost
$ 60,00012,0008,000
20.000$100,000
$250,000
$ 30,000
$ 20,000
$400,000
$ 80,000
$480,000
NOTES:
Cost estimate does not include operation, maintenance and monitoring costs for the IRAsystem at the southwestern portion of the NPI site (estimated 5 years of operation requiredunder this alternative).Assumes $5/cy to place on-site fill material in lagoon.
LLV59IO RPT
eder associates
NATIONAL PRESTO INDUSTRIES, INC.EAU CLAIRE, WISCONSIN
TABLE 14
PRELIMINARY CAPITAL COST ESTIMATE fVADQSE ZONE SOIDALTERNATIVE V-3 - COMPOSTING IN BIQPILES
Description
Excavate Soils
Composting in Biopiles
Return Treated Soil to Lagoon and Backfill
Engineering Design
Construction Administration
SUBTOTAL
Contingencies (@ 20%)
TOTAL
Estimated Cost
$ 1,800,000
$ 6,000,000
$ 850,000
$ 30,000
$ 40,000
$ 8,720,000
$ 1,744,000
$10,500,000
NOTES:
Cost estimate does not include operation, maintenance and monitoring costs for the IRAsystem at the southwestern portion of the NPI site (estimated 5 years of operation requiredunder this alternative).Assumes the following unit costs:
$15/cy to excavate soil from lagoon$50/cy for composting in biopiles$ 5/cy to place treated soil and on-site fill material in lagoon
LLV59SORPT
eder associates
NATIONAL PRESTO INDUSTRIES, INC.EAU CLAIRE, WISCONSIN
TABLE 15
PRELIMINARY CAPITAL COST ESTIMATE O/ADOSE ZONE SOIL^IALTERNATIVE V-4 - OFF-SITE LANDFILLING
Description
Excavate Soils
Off-site Transportation and Disposal
Backfill Lagoon
Engineering Design
Construction Administration
SUBTOTAL
Contingencies (@ 20%)
TOTAL
Estimated Cost
$ 1,800,000
$10,200,000
$ 850,000
$ 20,000
$ 30,000
$12,900,000
$ 2,580,000
$15,480,000
NOTES:
Cost estimate does not include operation, maintenance and monitoring costs for the IRAsystem at the southwestern portion of the NPI site (estimated 5 years of operation requiredunder this alternative).Assumes the following unit costs:
$15/cy to excavate soil from lagoon$85/cy for off-site transportation and disposal in a non-hazardous waste landfill(Source: Jackson County Landfill, Black River Fall, WI - from NPI FS report)$ 5/cy to place on-site fill material in lagoon
LLVS9»0 RPT
eder associates
NATIONAL PRESTO INDUSTRIES, INC.EAU CLAIRE, WISCONSIN
TABLE 16
PRELIMINARY CAPITAL COST ESTIMATE fWASTE/SOILIALTERNATIVE S-1 - CONSOLIDATE AT MRDS FOR CAPPING
Description
Move Waste/Soil from Temporary Stockpiles to MRDS
Engineering Design
Construction Administration
SUBTOTAL
Contingencies (@ 20%)
TOTAL
Estimated Cost
$ 70,000
$ 5,000
$ 5,000
$ 80,000
$ 16,000
$100,000
NOTES:
1. Assumes $7/cy to move waste/soil from stockpiles to MRDS.
LLV59IOWT
eder associates
NATIONAL PRESTO INDUSTRIES, INC.EAU CLAIRE, WISCONSIN
TABLE 17
PRELIMINARY CAPITAL COST ESTIMATE (WASTE/SOIL^)ALTERNATIVE S-4 - OFF-SITE LANDFILLING
Description
Remove Waste/Soil from Temporary Stockpiles and LoadOnto Trucks
Off-site Transportation and Disposal
Engineering Design
Construction Administration
SUBTOTAL
Contingencies (@ 20%)
TOTAL
Estimated Cost
$ 70,000
$ 850,000
$ 10,000
$ 10,000
$ 940,000
$ 188,000
$1,130,000
NOTES:
1. Assumes the following unit costs:$7/cy to remove waste/soil from stockpiles and load onto trucks$85/cy for off-site transportation and disposal in a non-hazardous waste landfill(Source: Jackson County Landfill, Black River Fall, WI - from NPI FS report)
LLVS9SORPT
FIGURES
eder associatesFIGURE 1
500'I
Scale In Feet
SITE PLANNATIONAL PRESTO INDUSTRIES, INC. SITE
EAU CLAIRE. WISCONSIN
Access Road
NPIUSSA- -NPRJSS8
Top Of Slope
Bottom Of Slope
0I
80I
Scale In Feet
112696SW49716D
LAGOON No. 1SAMPLING LOCATIONS
NATIONAL PRESTO INDUSTRIES, INC.EAU CLAIRE, WISCONSIN
© Soil Boring Location• Soil Grab Sample Location
(September 1996)A Soil Boring To Characterize
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B-1 Through B-7 DrilledIn September 1995
B-8 Through B-20 DrilledIn September 1996
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NPIUSSA- -NPIUSS8
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Bottom Of Slope
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LAGOON No. 1CROSS SECTION LOCATION
NATIONAL PRESTO INDUSTRIES, INC.EAU CLAIRE, WISCONSIN
© Soil Boring Location• Soil Grab Sample Location
(September 1996)k. Soil Boring To Characterize
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Cross Section Line
NOTBB-1 Through B-7 Drilled
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ff-ff Through B-20 DrilledIn September 1996
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All Concentrations In ppb LAGOON NO. 1
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LAGOON No.lVERTICAL PROFILE OF PCE CONCENTRATIONS
NATIONAL PRESTO INDUSTRIES, INC.EAU CLAIRE, WISCONSIN
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APPENDIX A
BORING LOGS AND BOREHOLE ABANDONMENT FORMS
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State ol WisconsinDepartment ot Na tu ra l Resources
Soil Boring Log Information SupplementForm 4400-122A 7.4
Boring Number B-l Use only as an attachment to Form 4400-122. Page 2 of 3Sample :
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Slate of Wiscons inDepartment of Natural Resources
WELL DRILLHOLE, BOREHOLE ABANDONMENTForm 3300-5W 11-89
All abandonment work shall he performed in accordance with theAdmin. Code, whichever is applicable. Also, see instructioas on
provisions of Chapters NR 1 1 1 . NR 112 or 141, Wis.back.
(1) GENERAL INFORMATIONWell/Drillhole/Borehole C
Location
1/4 of 1/4 of Sec.(It Applicable)
Gov't LotGrid Location
f, n N. n s
1 ( 2 ) FACILITY NAME Presto-ounty
Eau ClaireD E
• T. N; R. .. CD W
Grid Number
ft. HE. D w.Civil Town Name
Street Address of Well
City, Village
Eau Claire
original Wel l uwner di Known/
Present Well Owner
! PrestoStreet or Route
City, State. Zip CodeEau Claire, WI
Facility Well No. and/or Name
B-l(If Applicable) WI Unique Well No.
Reason For Abandonment
Test BoringDate of Abandonment
08/30/95WELL/DRILLHOLE; BOREHOLE INFORMATION(3) Original Well/Drillhole/Borehole Construction Completed On
(Datel
LJ Monitor ing WellD Water Well[3 Dri l lholeLJ Borehole
Construction Type:[X] Drilled CD Driven (PI Other rSper.fy^
Formation Type:C*J Unconsolidated Formation
Construction Report Available''C3 Yes D No
Sandpoint) LJ Dug
D Bedrock
Total Well Deplh (ft) Casing Diameter (ins J(From groundsurface)
Casing Depth i Ft .)
Was Well Annular Space Grouted. 'If Yes. To What Deplh?
IH Yes C No _ UnknownFeet
(7)Sealing Material Used
Bentonite Chips
(9) Name of Person or Firm Doing Sealit
Boajt J^onsvear ^.,Sign/wfe of Person QullTli WodT^'
fr~**~*— / r^^S^^If y ^^^\m **"Street or Route
101 Alderson StreetCity, State, Zip Code
(4) Depth in Water (Feet) Dry
Pump & Piping Removed? CD Yes CD No S Not ApplicableLiner(s) Removed? CD Yes CD No £3 Not ApplicableScreen Removed? CD Yes CD No [E3 Not ApplicableCasing Left in Place? CD Yes CD NoIf No, E x p l a i n
Was Casing Cut Off Below Surface? CD Yes CD NoDid Sealing Material Rise to Surface? S Yes CD NoDid Material Settle After 24 Hours? D Yes ^ NoIf Yes, Was Hole Retopped? CD Yes CD No
(5) Required Method of Placing Sealing MaterialK Conductor Pipe - Gravity CD Conductor Pipe - PumpedCD Dump Bailer D Other (Explain)
(6) Sealing Materials For monitoring wells and1 1 Neat Cement Grout monitoring well boreholes onlyCD Sand-Cement (Concrete) GroutLJ Concrete CD Benlonite Pellets1 i Clay-Sand Slurry LJ Granular Bentonitei _ 1 Bentonite Sand Slurry 1 _ 1 Bentomte-Ceir.ent GroutLA! Chipped Bentonite
No. YarFrom (Ft.) To (Ft.) Sacks Sea
or Volur
Surface 37.5 11 Bi
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DatpSignedjfgZ ~\ c c
(W^-^-^-ff>KVftX&KDai£:R-c«;Ne<Kbts£<£tta: : :•:•: :
Telephone Number } X-X-X-X X-X-X-X X-X-X-:- • -X(715)359-7090 ' iPaliow-iip-Nccessarv.-:-:-: : x :
3s,lant Mix Ratio or Mud Weightne
igs
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Schofield. WI 54476DNR/COUNTY
State of WisconsinDepartment ot Natural Resources
Route To:D Solid WasteD Emergency Responsed Wastewater
D Haz. Wasted Underground TanksI I Water ResourcesD Other
Soil Boring Log InformationForm 4400-122 7-91
Page 1 of 2Facility Project Name License/ Permit/Monitor ing Number
PrestoBoring Drilled By (F i rm
Boring NumberB-2
name and name of crew chief) Date D r i l l i n g Started Date D r i l l i n g Completed ^ D r i l l i n g MethodBoart Longyear-Eric Schoenberg
DNR Facility Well No. W] Unique Well No.
Boring LocationState Plane
1/4 of
8/30/95 8/30/95Common Well Name Final Static Water Level Surface Elevation I
B-2 Feet MSL Feet MSL
HSA
torehole Diameter
7.0 InchesLocal Grid Location (If applicable)
N, E
1/4 of SectionCounty
Eau ClaireSample
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I hereby certify that the information on this form is true and correct to the best of my knowledge.Signature Firm BOART LONGYEAR
101 Aldcrson Schofield, Wl 54476-0109Tel: (715) 359-7090 Fax: (715) 355-5715
This form is authorized by Chapters 144. 147 and 162, Wis. Slats. Completion of this report is mandatory. Penalties: Forfeit not less than S10 normore than S5.000 for each violation. Fined not less than $10 or more than $100 or imprisoned not less than 30 days, or both for each violation.Each day of cont inued v i o l a t i o n is a separate offense, pursuant to ss 144.99 and 162.06. Wis. Stats.
State •)[" WisconsinDepartment of Natural Resources
Soil Boring Log Intormauon SupplementForm 4400-1 22A 7-91
Boring Number B-2 Use only as an attachment to Form 4400-122. Page 2 of 2
Sample '
Num
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SL.tc of Wiscons inDepartment of N a t u r a l Resources
WELL D R I L L H O L E . BOREHOLE ABANDONMENTFurm 3300-5W 11-89
All abandonment work shall be performed in accordance with the provisions of Chapters NR 1 1 1 . NR 112 or 141, Wis.Admin. Code, whichever is applicable. Also, see instructions on back.(1) GENERAL INFORMATION 1(2) FACILITY NAME Presto
Well/Dnllhole/Borehole CountyLocat.on Eau Clajre
n E1/4 of 1/4 of Sec. ; T. N: R. CD W
( I f Applicable)
Gnv'r I nt Grid NumberGrid Location
ft. n N n s., rt. n E. n w.Civil Town Name
Street Address of Well
City, Village
Eau Claire
Original W e l l Owner ( i l Known)
I Present Well Owner1
PrestiStreet or Route
City, State, Zip Code
Eau Claire. WIFacility Well No. and/or Narm
B-2: (If Applicable) WI Unique Well No.
Reason For Abandonment
Test BoringDate of Abandonment
08/30/95WELL/ DRiLLHOLE/BOREHOLE INFORMATION(3) Original Well/Drillhole/Borehole Construction Completed On
mate)
LJ Monitoring Well Construction Report Available?D Water Well K Yes CD NoE3 DrillholeCD Borehole
Construction Type:^ Drilled CD Driven (Sandpoint) CD Dug[~1 Other (Specify)
Formation Type:K Unconsolidated Formation CD Bedrock
Total Well Depth (ftl Taxing Diameter f i n s . )(From groundsurface)
Casine Depth (Ft )
Was Well Annular Space Grouted? 1 _ ] Yes 1 _ 1 No ' _ UnknownIf Yes. To What Depth? Feet
(7)Sealing Material Used
Bentonite Chips
(4) Depth to Water (Feet) 2.9Pump &. Piping Removed?Liner(s) Removed?Screen Removed?Casing Left in Place?
D Yes D No ^ Not ApplicableD Yes D No S Not ApplicableD Yes D No S Not ApplicableD Yes D No
Was Casing Cut Off Below Surface? D Yes CD NoDid Sealing Material Rise to Surface? ^ Yes CD NoDid Material Settle After 24 Hours? CD Yes ^ NoIf Yes. Was Hole Retopped? CD Yes CD No
(5) Required Method of Placing Sealing MaterialS Conductor Pipe - Gravity CD Conductor Pipe - PumpedCD Dump Bailer CD Other (Explain)
(6) Sealing Materials For monitoring wells andCD Neat Cement Grout monitoring well boreholes onlyCD Sand-Cement (Concrete) GroutCD Concrete | CD Bentonite PelletsCD Clay-Sand Slurry ' CD Granular Bentonite! 1 Bentonite -Sand Slurry i LJ Bentonite -Cement Grout1X1 Chipped Bentonite
No. YaFrom (Ft . ) To (Ft.) Sacks Se
or Vol
Surface 30.5 10 E
rds..alant Mix Ratio or Mud Weightjme
tags
(8) Comments __ ———————————————————————————————————————————————————
(9) Name of Person or Firm Doing Sealing Work
BoanJ^ongyear ,SigigWre of Per SUM P U P I L Wo/fe/
tr~*^- / &*<£-*Street or Route
101 Alderson Street
Dape Signed
<~£1-/Z-Q5Telephone Number
(715)359-7090Ciry. State. Zip Code
Schofield. WI 54476
m^-:-:--:--:--:--:--:--:--f^KDaio:R«*lvc
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DNR/COUNTY
State nl Wiscons inDepartment ot N a t u r a l Resources
Route ToD Solid WasteI I Emergency ResponseQ Wastewater
_! Haz Waste_J Underground TanksD Water ResourcesD Other
Soil Boring Log InformationForm 4400-122 7.9!
Page 1 of 2Facility/Project Name
PrestoLicense/Permit/Monitoring Number Boring Number
B-3Boring Drilled By (Firm name and name of crew chief) Date Dril l ing Started Date Dri l l ing Completed
Boart Longyear-Eric Schoenberg
DNR Facility Well No. WI Unique Well No.
Boring LocationState Plane
1/4 of
8/31/95 8/31/95
Common Well Name i Final Static Water Level Surface Elevation 1B-3 1 Feet MSL Feet MSL
Drill ing Method
HSA
lorehole Diameter7.0 Inches
Local Grid Location i If applicable)N, E U« "' " n N a E
1/4 of SectionCounty
Eau ClaireSample |
Z
1
2
3
4
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2.0
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— 4
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66910
20 6
-7
-8
— 9
— 10
-1 1
f-P-
T N.R Long ° ' " Feet D S Feet D WDNR County Code18
Soil/Rock DescriptionAnd Geologic Origin For
Each Major Unit
Br Med. SAND and GRAVEL
GO
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Civil Town/City/ or VillageEau Claire
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I hereby certify that the information on this form is true and correct to the best of my knowledge.Signature Firm BOART LONGYEAR
101 Alderson Schoficld. WI 54476-0109Tel: (715) 359-7090 Fax: (715) 355-5715
This form is authorized by Chapters 144. 147 and 162. Wis. Stats Complet ion of th i s report is mandatory. Penalties: Forfeit not less than $10 normore than $5.000 for each v io la t ion . Fined not less than S10 ,ir more than S100 or imprisoned not less than 30 days, or both for each violation.Each day of continued v io la t ion is a separate offcnse. p u r s u a n t to ss 144 99 and 162.06. Wis. Stats.
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Blow Counts
Depth In Feet
Soil/Rock DescriptionAnd Geologic Origin For
Each Major Unit
u s e sGraphicLogWellDiagram
P1D/FID
StandardPenetrationMoistureContent g.Liquid 7Limit "fPlastic |Limit
P200
RQD/Comments
Cd
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2 c!E 3
•n c/2° O3 =-'*. CD£» f~.
? I'
-a"2.rt3re
Stale ol' WisconsinDepartment of Natura l Resources
All abandonment work shall he performed in accordance with theAdmin. Code, whichever is applicable. Also, see instructions on
WELL, D R I L L H U L L BUKhdOLL ABANDONMENTForm 3300-5W i 1-39
provisions of Chapters NR 1 1 1 , NR 112 or 141, Wis.hack.
(1) GENERAL INFORMATIONWell/Dnllhole/Boreholc CountyLocation Eau Qaire
D E1/4 of 1/4 nf Sec ; T. Ni R H W
(If Applicable)
Gov't I nt Grid NumberGrid Location
ft. n N. n s.. ft. HE. n w.Civil Town Name
Street Address of Well
City, Village
Eau Claire
(2) FACILITY NAME PrestoOriginal Well Owner (II Known)
Present Well OwnerPresto
Street or Route
City, State, Zip Code
Eau Claire^WIFacility Well No. and/or Name (If Applicable)
B-3Reason For Abandonment
Test Boring^Date of Abandonment
08/31/95
WI Unique Well No
WELL/DRJLLHOLE/BOREHOLE INFORMATION(3) Original Well/Drillhole/Borehole Construction Completed On
rDatel
1 1 Monitoring Well Construction Report Available?D Water Well [X] Yes D No£3 DrillholeD Borehole
Construction Type:E*3 Drilled CD Driven (Sandpoint) CD Dug(~1 Other (Specify)
(4) Depth to Water (FeeH Dry
Pump & Piping Removed? CD Yes [HI No £3 Not ApplicableLiner(s) Removed? CD Yes CD No S Not ApplicableScreen Removed? [ _ 1 Yes L J No 1X1 Not ApplicableCasing Left in Place? CD Yes CD NoIf No, Explain
Was Casing Cut Off Below Surface'' CD Yes CD NoDid Sealing .Material Rise to Surface1' CE3 Yes CD NoDid Material Settle After 24 Hours? CD Yes 1X1 NoIf Yes, Was Hole Retopped? CD Yes CD No
Formation Type:1X1 Unconsolidated Formation D Bedrock
(5) Required Method of Placing Sealing MaterialiXJ Conductor Pipe - Gravity CD Conductor Pipe - PumpedD Dump Bailer CD Other (Explain)
Total Well Depth (ft) Casing Diameter f ins.1(From groundsurface)
Casing Depth (Ftl
Was Well Annular Space Grouted? 1 I Yes 1 1 No 1 _ 1 UnknownIf Yes. To What Depth'.' Feet
(7)Sealing Material Used
Bentonite Chips
(6) Sealing Materials For monitoring wells andI _ 1 Neat Cement Grout monitoring well boreholes only1 1 Sand-Cement (Concrete) GroutCD Concrete CD Bentonite Pellets1 1 Clay-Sand Slurry CJ Granular Bentonite1 1 Bentonite -Sand Slurry 1 1 Bentonite-Cement GroutIXl Chipped Bentonite
From (Ft.)
Surface
To (Ft.)
20.0
No. Yards,Sacks Sealant
or Volume
7 Bags
Mix Ratio or Mud Weight
(8) Comments
(9) Name of Person or Firm Doing Sealing WorkBoartLongyear
SignjBWre of Person Doing
Street or Route
101 Alderson Street
Daft Signed
City, State. Zip Code
Schofield, WI 54476
Telephone Number
(715) 359-7090
DNR/COUNTY
This form is authorized hy Chapters 144, 147 and 162, W
is Stals
Completion
more than $5,000 for each violation.
Fined not less than $10 or more than SIOO
Each dav of continued violation is a separate offense. pursuant to ss 144 99 and
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8/31/95Drilling M
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orm 4400- 122
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Stale of WisconsinDepartment of N a t u r a l Resources
Soil Boring Log Information SupplementForm 4400-122A 7-91
Boring Number B-4 Use only as an attachment to Form 4400-122. Page 2 of 3
Sample
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State of WisconsinDepartment of Natural Resources
WE X/DR;LLHOLE. BOREHOLE ABANDONMENTForm 3300-5 »V 11.39
All abandonment work shall be performed in accordance with theAdmin. Code, whichever is applicable. Also, see instructions on
provisions of Chapters NR 1 1 1 , NR 112 or 141. Wis.back.
(1) GENERAL INFORMATIONWell/Drillholc/Borehole CountyLocalion Eau Claire
D E1/4 of 1/4 of Sec. ; T. N; R l ~ l w
(If Applicable)Oov't Lot Grid Number
Grid Locationft. n N. n s.. ft n F n w
Civil Town Name
Street Address of Well
City, Village
Eau Claire
(2t FACILITY NAME PrestoOriginal Well Owner (If Known)
Present Well Owner
PrestoStreet or Route
City, State, Zip Code
Eau Claire, WIFacility Well No. and/or Name
B-4Reason For Abandonment
Test BoringDate of Abandonment
08/31/95
(If Applicable) WI Unique Well No.
WELL/DRILLHOLE/BOREHOLE INFORMATION
(3) Original Well/Drillhole/Borehole Construction Completed On(Date)
CD Monitoring V/ell Construction Report Available?D Water Well E3 Yes D NoIE1 DrillholeD Borehole
Construction Type:IXI Drilled LJ Driven (Sandpoint) 1 1 DugPI Other (Specify^
Formation Type:[X] Unconsolidated Formation LJ Bedrock
Total Well Depth ffr t Casing Diameter (ins.)(From groundsurface)
Caxinp Depth (Ft )
Was Well Annular Space Grouted? CD Yes L~J No CH UnknownIf Yes, To What Depth'' Fret
(7)Sealing Material Used
Bentonite Chips
(4) Depth to Water (Feet) PrYPump & Piping Removed?Liner(s) Removed?Screen Removed?Casing Left in Place9
D Yes D No ^ Not ApplicableD Yes D No ^ Not ApplicableCD Yes D No IE] Not ApplicableD Yes D No
Was Casing Cut Off Below Surface? D Yes D NoDid Sealing Material Rise to Surface1 [*3 Yes D NoDid Material Settle After 24 Hours? D Yes IE] NoIf Yes, Was Hole Retopped? CD Yes D No
(5) Required Method of Placing Sealing Material£3 Conductor Pipe - Gravity CD Conductor Pipe - PumpedCD Dump Bailer CD Other (Explain)
(6) Sealing Materials For monitoring wells andCD Neat Cement Grout monitoring well boreholes onlyCD Sand-Cement (Concrete) GroutCD Concrete ', CD Bentonite PelletsCD Clay-Sand S l u r r y ' CD Granular Bentonite[ 1 Bentor.itc-Sand Slurry i 1 _ 1 Bentonite-Ccment Grout[XJ Chipped Bentonite
No. YaFrom (Ft.) To (Ft.) Sacks Se
or Vok
Surface 40.0 13 B
rds,alant Mix Ratio or Mud Weightme
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(9) Name of Person or Firm Doing Sealing WorkBoart Longyear
Sigaawfe of PersonJQoing Work"/
W-^- / <ujiCStreet or Route * "*
101 Alderson Street
Date Signed
?^-yz-9STelephone Number
(715)359-7090City, State, Zip Code
Schofield, WI 54476
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Stale of WisconsinDepartment of Natural Resources
W E L L / D R I L L H O L E , BOREHOLE ABANDONMENTForm 3300-5W H_ 8 9
All abandonment work shall be performed in accordance with the provisions of Chapters NR 1 1 1 . NR 112 or 141, Wis.Admin. Code, whichever is applicable. Also, see iastructions on back.(1) GENERAL INFORMATION | (2) FACILITY NAME Presto
Well/Drillhole/Borehole CountyLocation gau Claire
D E1/4 of 1/4 of Sec. : T N; R CD W
(If Applicable)Oov't Lot Grid Number
Grid Locationft. n N. n s.. ft HE. n w.
Civil Town Name
Street Address of Well
City, Village
Eau Claire
Original Wel l Owner ( I I Known)
Present Well Owner
PrestoStreet or Route
City. State, Zip Code
Eau Claire, WIFacility Well No. and/or Name (If Applicable) WI Unique Well No.
B-5Reason For Abandonment
Test BoringDate of Abandonment
08/31/95WELL/DRILLHOLE/BOREHOLE INFORMATION(3) Original Well/Drillhole/Borehole Construction Completed On
mute)
CD Monitoring WellCD Water Well[X] DrillholeD Borehole
Construction Report Available?Kl Yes D No
(d) rvpth m w^r (Pe.c-.tt DryPump & Piping Removed? D Yes D NoLiner(s) Removed? EH Yes D NoScreen Removed? D Yes D No 1Casing Left in Place'' D Yes D NoIf N" F.xpbiin
3 Not ApplicableXJ Not ApplicableXJ Not Applicable
Construction Type:03 Drilled CD Driven (Sandpoint) CD Dugn Other (Specify) __________________________
Formation Type:C*J Unconsolidated Formation D Bedrock
Was Casing Cut Off Below Surface? LJ Yes LJ NoDid Sealing Material Rise to Surface? [X] Yes D NoDid Material Settle After 24 Hours? D Yes £3 NoIf Yes, Was Hole Retopped? D Yes D No
(5) Required Method of Placing Sealing MaterialE3 Conductor Pipe - Gravity CD Conductor Pipe - PumpedCD Dump Bailer CD Other (Explain)
Total Well Depth (ftl Casing Diameter f ins t(From groundsurface)
Casing Depth (FM
Was Well Annular Space Grouted? CD Yes CD No LJ UnknownIf Yes To What Depth1' Feet
(7)Sealing Material Used
Bentonite Chips
(6) Sealing Materials For monitoring wells andCD Neat Cement Grout monitoring well boreholes onlyD Sand-Cement (Concrete) GroutCD Concrete CD Bentonite PelletsCD Clay-Sand Slurry CD Granular BentoniteI I Bcntonitc-Sand Slurry 1 _ 1 Bentonite-Cement Grout[X] Chipped Bentonite
From (Ft.)
Surface
To (Ft.)
28.0
No. Yards,Sacks Sealant
or Volume
8 Bags
Mix Ratio or Mud Weight
(8) Comments
(9) Name of Person or Firm Doing Sealing Work
Boart IjongyearSignafiirf' of Persoj^Jiauj^r-Worj^X/FV / t*J&LStreet or Route *"
101 Alderson StreetCity, State, Zip Code
Schofield. WI 54476
Data-SignedrfSL^-wTelephone Number
(715)359-7090
tifc:::::::::::::::::: :!;Da^:R-«*ke<}/tr^t;ied;-:-:-:-:-:-:-:-:-: :•:•:•:•: Dia-tia/CtiHiitY-:-: :•:•::•:•:•:•:•:•:•
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DNR/COUNTY
Stale of WisconsinDepartment of Na tu ra l Resources
Route To:D Solid WasteCD Emergency ResponseCD Wastewater
D Ha/. WasteCD Underground TanksCD Water ResourcesCD Other
Soil Boring Log InformationForm 44(X)-122 7-91
Page I of 2Facility/Project NamePresto
Boring Drilled By (Firm name and name of crew chief)Boart Longyear-Eric Schoenberg
DNR Facility Well No.
Boring LocationState Plane
1/4 ofCounty
Eau ClaireSample
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S1 • 1.0 | 1•
1
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2333
2334
4433
22**2
WI Unique Well No. Common WellB-6
Name
License/Permit/Monitoring
Date Drill ing Started
9/1/95
Final Static Water Level
N, E1/4 of Section
uuPL.
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Q-~-1-_ 2
-3
— 4
— 5
— 6
— 7
— 8
-9
— 10
— 112 _
E-12
T N,R
Feet MSL
Ut ° ' "
Long ° ' »DNR County Code18
Soil/Rock DescriptionAnd Geologic Origin For
Each Major Unit
Br Med. SAND and GRAVEL
00UonD
!
Number Boring NumberB-6
Date Dr i l l ing Completed
9/1/95Surface Elevation E
Feet MSL
Drill ing Method
HSA
orehole Diameter7.0 Inches
Local Grid Location (If applicable)CD N HE
Feet CD S Feet D WCivil Town/City/ or VillageEau Claire
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Soil Properties
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I hereby certify that the information on this form is true and correct to the best of my knowledge.Signature Firm BOART LONGYEAR
101 Alderson Schofield. WI 54476-0109Tel: (715) 359-7090 Fax: (715) 355-5715
This form is authorized by Chapters 144. 147 and 162, Wis. Stats. Completion of this report is mandatory Penalties: Forfeit not less than S10more than $5.000 for each violation. Fined not less than S10 or more than S100 or imprisoned not less than 30 days, or both for each violation.Each day of continued violation is a separate offcnse. pursuant to ss 144.99 and 162.06. Wis. Slats.
Stale of WisconsinDepartment of Natural Resources
Soil Boring Log Information SupplementForm 4400-122A 7-9!
Boring Number B-6 Use only as an attachment to Form 4400-122. Page 2 of 2
Sample
Num
ber
7 1
8 1•
9 I
10 I
11 1
12 I
13 I
14 I
15 ^1 __
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-18
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-22
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-26
— 273 :
so/ . ~28
Soil/Rock DescriptionAnd Geologic Origin For
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SANDSTONE
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EOB 28.5Backfill w/Holeplug
qj cd
£3 PID
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Soil Properties
O111? «Isoo CU
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State of WisconsinDepartment of Natura l Resources
Route To:Lj Solid WasteLJ Emergency ResponseLJ Wastewater
Soil Boring Log Information.] Haz. Waste
:. ! Underground TanksLJ Water ResourcesD Other
Form 4400-122 7-91
Page 1 of 2Facility/Project Name
National Presto Industries, Lagoon No. 1License/Permit/Monitoring Numher Boring Number
IB-6Boring Drilled By (Firm name and name of crew chief)Eric Schonberg, Boart-Longyear
Date Dr i l l ing Started
09/01/95Date D r i l l i n g Completed (Dri l l ing Method
09/01/95 HSA
DNR Facility Well No. iWI Unique Well No. Common Well
Boring LocationState Plane N, ESE l / 4 o f N W 1/4 of Section 35 T 28 N.R 9
CountyChippewa
Sample
1Z0
2
4
6
O8
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28
8
-1
-2
Name i Final Static Water Level Surface Elevation Borehole Diameter' Feet MSL ; Feet MSL 7.0 Inches
(Local Grid Location (If applicable)I L a < ° ' " D N L J E
W i Long ° ' " Feet D S Feet L] WDNR County Code Civil Town/City/ or Vil lage9 Eau Claire
: Soil Properties
Soil/Rock DescriptionAnd Geologic Origin For
Each Major Unit U
D1 " WASTE FORGE COMPOUND SPover dark brownSAND w/gravel
Same as above
-311
medium-coarse !
SP
I'M
O J
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^ 5
——
C5
Q •a •§ i" .P-, • i: ; •-• <u~-~^ "-* O *""O ; ^ C 'o 5CL
-4 i —————————————— ———————————— - —— , j — -: Brown medium SAND w/little coarse SP :^ sand. No gravel.-5 :
14 16 r~°
rL
12 6 h
i i
Brown medium-coarse SAND SP ;w/some fine sand and some gravel
6" GRAVEL w/sand over 6"1 - medium-coarse SAND
10
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brown GW '--' j ^
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1 12 7 }- Brown medium-coarse SAND SP |
L w/gravel t
8:07
Mi
8 10
'-12 —I hereby certify that the information on this form is true and correct to the best of my knowledge.Signature ^ Firm Eder Associates
8025 Excelsior Drive Madison, WI 53717Tel: (608)836-1500 Fax: (608)831-3337
This form is authorized by Chapters 144, 147 and 162, Wis . Stats. Completion of this report is mandatory Penalties: Forfeit not less than $10 normore than 55,000 for each vio la t ion . Fined not less than S10 or more than SlOO or imprisoned not less than 30 days, or both for each violation.Each day of continued violat ion is a separate offense. pursuant to ss 144.99 and 162.06, Wis. Stats.
State of WisconsinDepartment of Natural Resources
Soil Boring Log Information SupplementForm 4400-122A 7-91
Boring Number B-6 Use only as an attachment to Form 4400-122. Page 2 of 2Sample
4> f-l Dx> -5 >g 00 o5 co-3 fl> a>Z J OS
12 •
14 •
16 • 20
18 • 18
20 • 20
U22 • 18
1
24 • 18
t/5
OU
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17
10
26
13
18
20
g Soil/Rock Descriptionc And Geologic Origin For.c Each Major UnitE. 'uQ ;
Same as above.Two dark bands at bottom of spoon
-13 ; approx. 1/4" thick.
_ 14 ———————————————————————————————Brown medium -coarse SANDw/some fine sand. No gravel
-p iu Same as above.
Several bands of dark coloration as in-n spoon 12-14.
Same as above, grading to brownfine-medium SAND. No gravel
-19 :
6" same as above over brownfine-coarse SAND w/gravel.
-21
— 22 ——————————————————————————————; ; Brown fine-coarse SAND. No gravel.
inU00
SP
<s °ci 13 n?53 £Q
Soil Properties
i
QEQE
SP '
iSP !
t-* j
S3 S
11oo & 11Su
T3'11J J
M
M
M
SP
SP
SP !
-23
|-
24 f- Same as above with some dark 1/8 to
26 • 14 8
1/4" bands of coloration.-25
- 4" same as above over 4" smallh GRAVEL over 6" brown r
-27 L \fine-medium SAND. \^
:
; i
1
SP : 1
SP
L— --i: .. j
M
M
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is ECL J
i
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8(NQ.
eu
a 1& u8:15
8:19
8:25
8:27
8:35
8:39
8:42
8:47
28 6 50/6 6 same as above with a large cobbler\over whitish/brown SANDSTONE /
EOB @ 28.5 feetWhitish/Brown fine grained, friableSANDSTONE.
SP--"
M o:ji
Suite of WisconsinDepartment of Natural Resources
WE .L. DRILLHOLE BOREHOLE ABANDONMENTForm 3300-5 vv 11-89
All abandonment work shall he performed in accordance with theAdmin. Code, whichever is applicable. Also, see instructions on
provisioas of Chapters NR 1 1 1 , NR 112 or 141, Wis.back.
(1) GENERAL INFORMATIONWell/Drillholc/BoreholeLocation
1/4 of 1/4 of Sec.(If Applicable)
Gov't LotGrid Location
ft. n N. n s..
County
Eau ClaireD E
; T. N; R FI W
Grid Number
ft n F. n w.Civi l Town Name
Street Address of Well
City, Village
Eau Claire
(2) FACILITY NAME PrestoOriginal Well Owner (If Known)
Present Well Owner
PrestoStreet or Route
City, State, Zip Code
Eau Claire. WIFacility Well No. and/or Name
B-6Reason For Abandonment
Test BoringDate of Abandonment
09/01/95
(If Applicable) WI Unique Well No.
WELL/DRJLLHOLE/BOREHOLE INFORMATION(3) Original Well/Drillhole/Borehole Construction Completed On
matel
1 1 Monitoring WellD Water Well[X] DrillholeCD Borehole
Construction Type:E3 Drilled CD Drivenl~1 Other fSpecifvl
Formation Type:1X3 Unconsolidated Formation
Construction Report Available'7
0 Yes D No
(Sandpoint) CD Dug
D Bedrock
Total Well Depth Ift) Casine Diameter f i n s 1(From groundsurface)
Casing Depth (Ft . l
Was Well Annular Space Grouted?If Yes, To What Depth?
D Yes n No D UnknownFeel
(7)Sealing Material Used
Bentonite Chips
(4) Depth to Water (Feet) PryPump & Piping Removed?Liner(s) Removed?Screen Removed?Casing Left in Place?I f Nn, Fxplain
D Yes CD No Kl Not ApplicableD Yes D No S Not ApplicableD Yes CD No K! Not ApplicableD Yes D No
Was Casing Cut Off Below Surface? CD Yes CD NoDid Sealing Material Rise to Surface? [3 Yes CD NoDid Material Settle After 24 Hours? CD Yes E3 NoIf Yes. Was Hole Retopped? CD Yes CD No
(5) Required Method of Placing Sealing MaterialPsl Conductor Pipe - Gravity CD Conductor Pipe - Pumped! 1 Dump Bailer CD Other (Explain)
(6) Sealing Materials For monitoring wells andCD Neat Cement Grout monitoring well boreholes onlyCD Sand-Cement (Concrete) GroutCD Concrete CD Bentonite PelletsCD Clay-Sand Slurry CD Granular Bentonite1 1 Bentonite -Sand Slurry CD Bentonite-Cement GroutiXJ Chipped Bentonite
No. YaFrom (Ft.) To (Ft.) Sacks Se
or Vok
Surface 28.5 10 B
rds,alant Mix Ratio or Mud Weightme
ags
i8) Comments
(9) Name of Person or Firm Doing Sealing Work
Boart.Ljgngyear______f Perso
Street or Route
101 Alderson StreetCity. State, Zip Code
Schofield, WI 54476
Date/Signed
Telephone Number
(715)359-7090
DNR/COUNTY
State of WisconsinDepartment of Natura l Resources
Route To:D Solid WasteCD Emergency ResponseI I Wastewatcr
Soil Boring Log InformationCH Ha/,. WasteCD Underground TanksI I Water ResourcesD Other
Form 4400-122 7-91
Page 1 of 2Facility/Project NamePresto
Boring Drilled By (Firm name and name of crew chief)Boart Longyear-Eric Schoenberg
DNR Facility Well No.
Boring LocationState Plane
1/4 ofCounty
Eau ClaireSample
£•&
1 6 21 £?83 OJ UZJ3«1 • 2.0
2 • 2.0
C
OU_0324710
2M ; 2
1 3
1i
1 — !
1 20•| •
q
5
345
WI Unique Well No. Common WellB-7
Name
License/PermityMonitoring
Date Dri l l ing Started
8/31/95
Final Static Water Level
N, E1/4 of Section
5uUL
•5Q
--
-1_
-2-"-3I:—4
-
-5
— 6
— 7
-8
--9-
-10
_-11
8 iF-12
T N.R
Feet MSL
Lat ° ' "
Long ° ' "DNR County Code18
Soil/Rock DescriptionAnd Geologic Origin For
Each
Br Med. SAND
Major Unit
and GRAVEL
toUonD
Civil Town/CityEau Claire
o
n' 60i-l O
O -JO .
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— 60
i£ Q
Number Boring NumberB-7
Date Dri l l ing Completed JDr i l l i ng Method
8/31/95
Surface ElevationFeet MSL
HSA
Borehole Diameter7.0 Inches
Local Grid Location (If applicable)n N
Feet D S/ or Village
QOuQEL
D EFeet D W
Soil Properties
_o"2 aC^ l-i•g s2 S
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i
1 hereby certify that the information on this form is true and correct to the best of my knowledge.Signature Firm BOART LONGYEAR
101 Alderson Schofield, WI 54476-0109Tel: (715) 359-7090 Fax: (715) 355-5715
This form is authorized by Chapters 144, 147 and 162, Wis Stats. Completion of this report is mandatory. Penalties: Forfeit not less than S10 normore than 55,000 for each violation. Fined not less than $10 or more than $100 or imprisoned not less than 30 days, or both for each viola t ionEach day of continued violation is a separate offense, pu r suan t to ss 144.99 and 162.06. Wis. Stats.
sc
co mo O
5 o£ b
0
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4*.
Ul
g
on
ZDonHOZm
X X X X X X X . X . X
LAO
O O D O
Number
^ength (in)Recovered
Blow Counts
Depth In Feet
0. Om n =g o ?33- 2. 2
&. o' O0 ,-, ft-i O egr- — •3 C2. -5'
u s e sGraphicLogWellDiagram
P1D/F1D
StandardPenetrationMoistureContentLiquidLimitPlasticLimit
P200
RQD/Comments
y•o_n
£TJ
VI
03O
Zc3
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00
-a•aFT
State of WisconsinDepartment of Natural Resources
WELL, DRILLHOLE, BOREHOLE ABANDONMENTForm 33(X)-5W 1 1-H9
All abandonment work shall be performed in accordance with theAdmin. Code, whichever is applicable. Also, see instructioas on
provisions of Chapters NR 1 1 1 , NR 112 or 141, Wis.back.
(1) GENERAL INFORMATION j ( 2 ) FACILITY NAME PrestoWell/Drillhole/Borchole CountyLocation Eau Claire n E
1/4 of 1/4 of Sec ; T. N; R Cl W(If Applicable)
Gov't Lot Grid NumherGrid Location
ft. n N. n s f, n P n wCivil Town Name
Street Address of Well
City, Village
Eau Claire
Original Well Owner (If Known;
Present Well OwnerPresto
Street or Route
City, State, Zip Code
Eau Claire, WIFacility Well No. and/or Name (If Applicable) WI Unique Well No.
B-7Reason For Abandonment
Test BoringDate of Abandonment
08/31/95WELL/DRILLHOLE/BOREHOLE INFORMATION(3) Original Well/Drillhole/Borehole Construction Completed On
fDate^
1 1 Monitoring Well Construction Report Available1 'D Water Well [3 Yes D No1EI DrillholeD Borehole
Construction Type:E*] Drilled CD Driven (Sandpoint) CD DugPI Other ^.Specify}
Formation Type:LA] Unconsolidated Formation 1 1 Bedrock
Total Well Depth lft\ Casing Diameter f i n s . l(From groundsurface)
Casing Depth I f t . )
Was Well Annular Space Grouted? 1 _ 1 Yes i _ 1 No 1 _ I UnknownIf Yes. To What Depth'' Feet
(7)Sealing Material Used
Bentonite Chips
(4) Depth to Water (Feet) DryPump & Piping Removed? CD Yes CD No S Not ApplicableLiner(s) Removed? CD Yes CD No S Not ApplicableScreen Removed? CD Yes CD No [3 Not ApplicableCasing Left in Place? CD Yes CD No
Was Casing Cut Off Below Surface? CD Yes CD NoDid Sealing Material Rise to Surface? [3 Yes CD NoDid Material Settle After 24 Hours? CD Yes £3 NoIf Yes, Was Hole Retopped? CD Yes CD No
(5) Required Method of Placing Sealing MaterialD*J Conductor Pipe - Gravity 1 _ 1 Conductor Pipe - PumpedCD Dump !?•»"" CD Other (Explain)
(6) Sealing Materials For monitoring wells andCD Neat Cement Grout monitoring well boreholes onlyCD Sand-Cement (Concrete) GroutCD Concrete CD Bentonite PelletsCD Clay-Sand Slurry CD Granular BentoniteCD Bentonite-Sand Slurry LJ Bentonite-Cement GroutLA] Chipped Bentonite
No. Yards,From (Ft.) To (Ft.) Sacks Sealant Mix Ratio or Mud Weight
or Volume
Surface 20.0 6 Bags
i8) Comments
(9) Name of Person or Firm Doing Sealing Work
Boact-LpngyearSignaGMTof Persoj^Qftiag.Wort-*/'' Date Signed/F- y /'i,Z_^'/P-9sStreet or Route " "" Telephone Number
101 Alderson Street (715)359-7090City, State, Zip Code
Schofield, Wl 54476
fci9J:::::->:::::::::::::: :I3Hfc:&I?:&^Dattili^ivaJ/lir^et^^^
Rcvww'/JtepjMdr^'-:-:-:-:-:-:-:-:-:-:-:-:-:-:-:-:-:-:-:-:-:-:-:-:-:-:-:-:-:-:-:-:-:-:-:-:-:-:-:-:-:-:-:':-: :
iRalfosv-up-Necessary •:•:•:•:•:•:•:•:•:•:•:•:•:•:•:•:•:•:•:•:•:•:•:•:•:•:•:•:•:•:•:•:•:•:•:•:•:•:•:•:•:•:•:•:•:
DNR/COUNTY
State of WisconsinDepartment of Natura l Resources
Route To:D Solid WasteC3 Emergency ResponseC] Wastewater
D Haz. Wastel~l Underground Tanksn Water ResourcesD Other
Soil Boring Log InformationForm 4400-122 7-91
Page 1 of 4Facility/Project Name
National Presto Industries-Lagoon No. 1Boring Drilled By (Firm name and name of crew chief)
Boart Longyear (Mike Mueller)
DNR Facility Well No. WI Unique Well No.
Boring LocationState Planesw 1/4 of SE 1/4 of Section 34
Common Well
N, ET 28 N , R 9
CountyChippewa
Sample
Num
ber
!I
Leng
th (
in)
Reco
vere
d
12.5
195
tsiC0U0
CO4985
2775
7745
13UiC
-Co.Q
-I
-2
-4
jj-5
—6
—7
-8
-9
-10
.-11
-12
Name
W
License/Permit/Monitoring
Date Drilling Started
09/18/96
Final Static Water LevelFeet MSL
1
Lat ° ' "-ong ° ' "
DNR County Code9
Soil/Rock DescriptionAnd Geologic Origin For
Each Major Unit
Black medium to coarse sand, few gravel
Same as above
Same as above toBrown medium to
10.5 feetcoarse sand
onU
DSW
Number Boring NumberB-8
Date Dri l l ing Completed
09/18/96
Surface ElevationFeet MSL
Drilling Method
HSA
Borehole Diameter7.0 Inches
Local Grid Location (If applicable)D N D E
Feet D S Feet D WCivil Town/City/ or VillageEau Claire
0
D.a oo6.3i
r r p pP P P Pr P P Pp p » p
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p p P Pp p P PP P P Pr p p pp r p p
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Soil Properties
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men
ts
11:05
11:15
11:25
I hereby certify that the information on this form is true and correct to the best of my knowledge.Signature Firm g^er Associates
8025 Excelsior Drive Madison, WI 53717Tel: (608)836-1500 Fax: (608)831-3337
This form is /UithOrizeii by Chapters 144, 147 and 162, Wis. Stats. Completion of this report is mandatory. Penalties: Forfeit not less than $10 normore than $5,000 for each violation. Fined not less than SIO or more than $100 or imprisoned not less than 30 days, or both for each violation.Each day of continued violation is a separate offense, pursuant to ss 144.99 and 162.06, Wis. Stats.
1 — ^M^ H 1 MaajBBK)
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r p p r P P » P P P P P P r P r r r r ^ r p p p p p p p p * ' * * ' ' ' * ' ' ' ' ' ^ * ' 1 ' ' ' * ' * * * * '_*_'_* " * * * * * ' T * * * * * * ^ * * * * * * * * * * * * * * * ^ ^ * ^ ^ . * ^ ^ ^ ^ ^ . ^ » » »
2 2
§ I
Number mLength (in) "H.Recovered
Blow Counts
Depth In Feet
Soil/R
ock Description
And G
eologic Origin For
Each Major U
nit
u s e sGraphicLogWellDiagram
PID/FID
StandardPenetrationMoistureContent $Liquid 3>Limit -aPlastic s
VI
Limit
P200
RQD/Comments
03O
a
Z
o•-i
0300
Use only as an attachment to Form
44
sh-ihO
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State of WisconsinDepartment of Natural Resources
Soil Boring Log Information SupplementForm 4400-122A 7-91
Boring Number B-8 Use only as an attachment to Form 4400-122. Page 3 of 4Sample
Num
ber
Leng
th (
in)
| Rec
over
ed
• 20I
19
ROUo5
5102126
10253034
£J3H.Q
•
-33
-34
-35
-36
-37
-38
r39
—40
-41
-42
-43
—44
r45
-46
-47
-48
-49
-50
.-51-
-52
Soil/Rock DescriptionAnd Geologic Origin For
Each Major Unit
Same as above
Same as above
GOUC/3D
0exrt W)
62
1 1:i*X***
X'X*•^*X*•X»X
'X'l*i|i|:|:
>X*i*x'>£p^r^p^p
p p * Pr r rp P P P
P r Pp P p P
P p Pp p p pP p P
P P p PP p Pp p p pP r Pp P p »
p » p pp P P pp p P p
P p P
p P p rP P P r
r P p
P P PP P P P
P P P PP P P P
P P PP P P P
P P PP P P P
P P PP P P P
p P r rp p r P
P p PP p P Pp p p P
p p p pP p p Pr t rk k k k
k k k k
k k k kfc k « k
k k k *
k » k kk k k k
k k, k ftk k k k
X'X*
k k k kk k k kk k k k
k k k k
k k k k
1
£i PID
/FID
Soil Properties
Stan
dard
[Pen
etra
tion
Moi
sture
Cont
ent
M
M
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11
0 ^
e/i *Cr3 CE j
8CNCu RQ
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ents
12:10
12:25
co tr
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fllf3s* Scrt *-< <tn _ aC CL p
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'
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Number
Length (in)Recovered
Blow Counts
Depth In Feet
3 OOa. oS1 o -ET O_ o
to ""' i j
i O <*>3 <§:!•r^ S3 ^
T1 °
u s e sGraphicLogWellDiagram
PID/FID
StandardPenetrationMoistureContentLiquidLimitPlasticLimit
P200
RQD/Comments
inta
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GO
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5 f63 ona ns, o2 SS 5"
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oaOn•a"H.rTm3
State of WisconsinDepartment of Natural Resources
WELL/DRILLHOLE/BOREHOLE ABANDONMENTForm3300-5W 11-89
All abandonment work shall be performed in accordance with theAdmin. Code, whichever is applicable. Also, see instructions on
provisions of Chapters NR 111, NR 112 or 141, Wis.back.
t GENERAL INFORMATIONWell/Drillhole/Borehole CountyLocation EaU Qaire
D El /4of IMofSec -T. N; R (~1w
(If Applicable)
Hov't Lot Grid NumberGrid Location
ft n N n s.. ft. n F. n wCivil Town Name
Street Address of Well
City, Village
Chippewa Falls
(2) FACILITY NAME PRESTOOriginal Well Owner (It Knownj
Present Well Owner
PRESTOStreet or Route
City, State, Zip CodeChippewa Falls, WI
Facility Well No. and/or Name (If Applicable) WI Unique Well No.
B-8Reason For Abandonment
Test BoringDate of Abandonment
9-18-96WELL/DRILLHOLE/BOREHOLE INFORMATION(3) Original Well/Drillhole/Borehole Construction Completed On
(Date)
CD Monitoring WellD Water Well£3 DrillholeD Borehole
Construction Type:S Drilled D DrivenPI Other ^Specify1!
Formation Type:M Unconsolidated Formation
Construction Report Available?El Yes D No
(Sandpoint) LJ Dug
D Bedrock
Total Well Depth (ft) Casinir Diami-tpr f ins 1(From groundsurface)
rasing Depth (Ft ^
Was Well Annular Space Grouted?If Yes, To What Depth?
D Yes D No D UnknownFeet
(7)Sealing Material Used
Bentonite Chips
(4) Depth tPump &Liner(s)ScreenCasingIf No, E
T Water (Feert 57.8
Piping Removed? D Yes D No 03 Not ApplicableRemoved? D Yes D No S Not Applicable
Removed? D Yes D No 0 Not ApplicableLeft in Place? D Yes D No.iplain
Was Casing Cut Off Below Surface?Did Sealing Material Rise to Surface?Did Material Settle After 24 Hours?If Yes, Was Hole Retopped?
D Yes D No03 Yes D NoD Yes 03 NoD Yes D No
(5) Required Method of Placing Sealing MaterialS Conductor Pipe - Gravity d Conductor Pipe - PumpedD Dump Bailer D Other (Explain)
(6) Sealing MaterialsCH Neat Cement GroutCD Sand-Cement (Concrete) Grout1 1 ConcreteD Clay-Sand SlurryCD Bentonite-Sand SlurryS Chipped Bentonite
From (Ft.)
Surface
No. Yards,To (Ft.) Sacks Sealant
or Volume
60.5 18 Bags
For monitoring wells andmonitoring well boreholes only
D Bentonite PelletsLJ Granular Bentonite1 1 Bentonite-Cement Grout
Mix Ratio or Mud Weight
(9) Name of Person or Firm Doing Sealing WorkBoart Longyear
Signature of Person Doing Work
Street or Route "101 Alderson Street
Date Signed
Telephone Number(715) 359-7090
City, State, Zip Code
Schofield, WI 54476
(JOfcxixixSxiFjBfcjliip-
Rcit'wwr/'.Iro^iKkJF: : :
RqlR>w:up:fieciKsiqY. :
> : £DixHii
£:j ; •
DNR/COUNTY
State of WisconsinDepartment of Natural Resources
Route To:D Solid Wastel~l Emergency Responsel~l Wastewater
D Haz. Wastel~l Underground Tanksl~l Water ResourcesD Other
Soil Boring Log InformationForm 4400-122 7-91
Page 1 of 4Facility /Project Name
National Presto Industries-Lagoon No. 1Boring Drilled By (Firm name and name of crew chief)
Boart Longyear (Mike Mueller)
DNR Facility Well No.
Boring LocationState PlaneSW l / 4 o f S E
CountyChippewa
Sample
§u1 621 pz \3xm 1S
• 1811•
J 21
CO
S0U
O52443
4478
7688
OJU
U.
5Q
-.-1:
-2
-3
-4
-5
—6
—7
D— o
-9
WI Unique Well No.
1/4 of Section 34
-10
.-1;
-12
Common Well
N, ET 28 N,R 9
Name
W
License/Permit/Monitoring Number
Date Dri l l ing Started
09/18/96
Final Static Water LevelFeet MSL
Lat ° ' "
Long ° ' "DNR County Code9
Soil/Rock DescriptionAnd Geologic Origin For
Each Major Unit
Black medium to coarse sand
Same as above
Same as above toBrown medium to
10.5 feetcoarse sand
COUonDSW
Boring NumberB-9
Date Drilling Completed
09/18/96
Surface ElevationFeet MSL
Drilling Method
HSA
Borehole Diameter7.0 Inches
Local Grid Location (If applicable)n N
Feet D SD E
Feet D WCivil Town/City/ or VillageEau Claire
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I hereby certify that the information on this form is true and correct to the best of my knowledge.Signature Firm Associates
8025 Excelsior Drive Madison, WI 53717Tel: (608)836-1500 Fax: (608)831-3337
This formW authcfiz^by Cha&»l's"l44, 147 and 162, Wis, Stats. Completion of this report is mandatory. Penalties: Forfeit not less than $10 normore than $5,000 for each violation. Fined not less than $10 or more than $100 or imprisoned not less than 30 days, or both for each violation.Each day of continued violation is a separate offense, pursuant to ss 144.99 and 162.06, Wis. Stats.
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State of WisconsinDepartment of Natural Resources
WELL/DRILLHOLE/BOREHOLE ABANDONMENTForm3300-5W 11-89
All abandonment work shall be performed in accordance with theAdmin. Code, whichever is applicable. Also, see instructions on
provisions of Chapters NR 111, NR 112 or 141, Wis.back.
> GENERAL INFORMATIONWell/Drillhole/Borehole CountyLocation £&u C|aire
D E1/4 of 1/4 of Sec. ;T. N; R. Dw
(If Applicable)
Gov'f Ijnt Grid NumberGrid Location
ft. n N. n s.. ft. n E. n w.Civil Town Name
Street Address of Well
City, VillageChippewa Falls
(2) FACILITY NAME PRESTOOriginal Well Owner (If Known)
Present Well Owner
PRESTOStreet or Route
City, State, Zip CodeChippewa Falls, WI
Facility Well No. and/or Name (If Applicable) WI Unique Well No.B-9
Reason For AbandonmentTest Boring
Date of Abandonment9-18-96
WELL/DRILLHOLE/BOREHOLE INFORMATION<3) Original Well/Drillhole/Borehole Construction Completed On
(Date)
CD Monitoring WellD Water WellS DrillholeD Borehole
Construction Type:K Drilled CD DrivenC~l Other (SpeciM
Formation Type:£3 Unconsolidated Formation
Construction Report Available?E Yes D No
(Sandpoint) CD Dug
D Bedrock
Total Well Depth (ft) Casinff Diameter (in<; }(From groundsurface)
Casing Depth (Ft.}
Was Well Annular Space Grouted?If Yes, To What Depth?
D Yes D No D UnknownFeet
(7)Sealing Material Used
Bentonite Chips
(4) Depth tPump &Liner(sScreenCasingI f N o . E
i Water (F«-f) 54.0
Piping Removed? CD Yes D No S Not ApplicableRemoved? CD Yes D No ^ Not Applicable
Removed? CD Yes D No K Not ApplicableLeft in Place? CD Yes CD Noiplain
Was Casing Cut Off Below Surface?Did Sealing Material Rise to Surface?Did Material Settle After 24 Hours?If Yes, Was Hole Retopped?
D Yes CD NoS Yes D NoCD Yes E3 NoD Yes D No
(5) Required Method of Placing Sealing MaterialK Conductor Pine - Gravity CD Conductor Pipe - PumpedD Dump Bailer CD Other (Explain)
(6) Sealing MaterialsCD Neat Cement Grout1 1 Sand-Cement (Concrete) GroutI 1 Concrete1 _ 1 Clay-Sand SlurryCD Bentontte-Sand SlurryS Chipped Bentonite
From (Ft.)
Surface
No. Yards,To (Ft.) Sacks Sealant
or Volume
56.5 17 Bags
For monitoring wells andmonitoring well boreholes only
CD Bentonite PelletsCD Granular BentoniteCD Bentonite-Cement Grout
Mix Ratio or Mud Weight
(8) Comments
(9) Name of Person or Firm Doing Sealing WorkBoart Longyear
mature of Person Doing y/ork
Street or Route101 Alderson Street
City, State, Zip Code
Schofield, WI 54476
Date Signed
Telephone Number(715) 359-7090
DNR/COUNTY
State of WisconsinDepartment of Natural Resources
Route To:D Solid Waste0 Emergency ResponseD Wastewater
D Haz. WasteD Underground TanksD Water ResourcesD Other
Soil Boring Log InformationForm 4400-122 7-91
Page 1 of 3Facility/Project Name License/Permit/Monitoring Number
National Presto Industries-Lagoon No. 1Boring Drilled By (Firm name and name of crew chief) Date Drilling Started
Boart Longyear (Mike Mueller)
DNR Facility Well No.
Boring Location
WI Unique Well No.
State Planesw 1/4 of SE 1/4 of Section 34
CountyChippewa
Sample
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09/20/96
Common Well Name Final Static Water LevelFeet MSL
N, E Lat ° ' "T 28 N,R 9 W Long ° ' "
DNR County Code9
Soil/Rock DescriptionAnd Geologic Origin For
Each Major Unit
Black medium to coarse sand fromground surface to
Brown medium to
Same as above
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coarse sand
U
DSW
Boring NumberB-10
Date Dri l l ing Completed
09/20/96
Drilling Method
HSA
Surface Elevation Borehole DiameterFeet MSL 7.0 Inches
Local Grid Location (If applicable)D N D E
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I hereby certify that the information on this form is true and correct to the best of my knowledge.Signature Firm Eder Associates
8025 Excelsior Drive Madison, WI 53717Tel: (608)836-1500 Fax: (608)831-3337
This form i^auth^A^d^by £liap/te^sK144, 147 and 162, Wis. Stats. Completion of this report is mandatory. Penalties: Forfeit not less than $10 normore than $5,000 for each vioUffon. Fined not less than $10 or more than SiOO or imprisoned not less than 30 days, or both for each violation.Each day of continued violation is a separate offense, pursuant to ss 144.99 and 162.06, Wis. Stats.
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P200
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State of WisconsinDepartment of Natural Resources
Route To:D Solid WasteO Emergency Responsel~l Wastewater
D Haz. Wastel~l Underground Tanksl~l Water ResourcesD Other
Soil Boring Log InformationForm 4400-122 7.91
Page 1 of 1Facility/Project Name License/Permit/Monitonng Number
National Presto Industries-Lagoon No. 1Boring NumberB-21
Boring Drilled By (Firm name and name ot crew chief) Date Dril l ing Started Date Dril l ing CompletedBoart Longyear (Mike Mueller)
DNR Facility Well No. WI Unique Well No.
Boring LocationState PlaneSW 1/4 of SE 1/4 of Section 34
CountyChippewa
Sample
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12
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oCQ3556
6576
3344
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-3
-4
-5
-6
—7
09/24/96 09/24/96
Dril l ing Method
HSA
Common Well Name Final Static Water Level Surface Elevation Borehole Diameter
Feet MSL Feet MSL 7.0 InchesLocal Grid Location (If applicable)
N, ET 28 N,R 9 W I
1 -, u 1 »Lat D N D E_x>ng ° ' " Feet D S Feet D W
DNR County Code9
Soil/Rock DescriptionAnd Geologic Origin For
Each Major Unit
Black-brown medium to coarse sand
Brown medium to
Same as above
coarse sand
EOB @ 7 feet
C/3uDSW
Civil Town/City/ or VillageEau Claire
CJ
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men
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13:45
13:50
13:55
I hereby certify that the information on this form is true and correct to the best of my knowledge.Signature Firm Eder Associates
8025 Excelsior Drive Madison, WI 53717Tel: (608)836-1500 Fax: (608)831-3337
This form is au'thor#e<Kby Chapmen'144, 147 and 162, Wis. Stats. Completion of this report is mandatory. Penalties: Forfeit not less than $10 normore than $5.000 for each violation. Fined not less than $10 or more than $100 or imprisoned not less than 30 days, or both for each violation.Each day of continued violation is a separate offense, pursuant to ss 144.99 and 162.06, Wis. Stats.
State of WisconsinDepartment of Natural Resources
Route To:D Solid Wastel~l Emergency Response[~1 Wastewater
D Haz. Wastel~l Underground TanksC] Water ResourcesD Other
Soil Boring Log InformationForm 4400-122 7-91
Page 1 of 1Facility/Project Name License/Permit/Monitoring Number
National Presto Industries-Lagoon No. 1Boring NumberB-22
Boring Drilled By (Firm name and name ot crew chief) Date Drilling Started Date Drill ing CompletedBoart Longyear (Mike Mueller) 09/24/% 09/24196
Dril l ing Method
HSA
DNR Facility Well No. WI Unique Well No. Common Well Name Final Static Water Level Surface Elevation Borehole Diameter
FeetMSL Feet MS L 7.0 InchesBoring Location Local Grid Location (If applicable)State Plane N, E Lat ° ' " Q N j-j E
SW l / 4 o f S E 1/4 of Section 34 T 28 N . R 9 W Long Ol" Feet D S Feet D WCounty DNR County Code
Chippewa 9Sample
Num
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3357
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Soil/Rock DescriptionAnd Geologic Origin For
Each Major Unit
Brown oily medium to coarse sand
Brown medium to coarse sand
Same as above
EOB @ 4.5 feet
U
SW
Civil Town/City/ or VillageEau Claire
J3& 00
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SiQiU14:05
14:10
I hereby certify that the information on this form is true and correct to the best of my knowledge.Signature Firm g^er Associates
8025 Excelsior Drive Madison, WI 53717Tel: (608)836-1500 Fax: (608)831-3337
This form is^utho'r&e&fy Chag^*/144, 147 and 162, Wis. Stats. Completion of this repon is mandatory. Penalties: Forfeit not less than $10 normore than $5,000 for each violation. Fined not less than $10 or more than $100 or imprisoned not less than 30 days, or both for each violation.Each day of continued violation is a separate offense, pursuant to ss 144.99 and 162.06, Wis. Stats.
State of WisconsinDepartment of Natural Resources
Route To:D Solid WasteC] Emergency ResponseD Wastewater
D Haz. WasteD Underground Tanksl~l Water ResourcesD Other
Soil Boring Log InformationForm 4400-122 7-91
Page 1 of 1Facility/Project Name
National Presto Industries-Lagoon No. 1Boring Drilled By (Firm name and name of crew chief)
Boart Longyear (Mike Mueller)
DNR Facility Well No. WI Unique Well No. Common Well Name
License/Permit/Monitoring
Date Drilling Started
09/24/96
Tinal Static Water Level
Boring LocationStatesw
Plane1/4 of SE
CountyChippewa
Sample
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Feet MSL
Lat ° ' "
Long ° ' "DNR County Code9
cL<uQ
-1
—2
-3
—4
-5
-6
— 7
-8
-9
Soil/Rock DescriptionAnd Geologic Origin For
Each Major Unit
Black-brown oily medium to coarse sa~"!
Same as above
Same as above
Same as aboveBrown medium to coarse sand
BOB @ 9.5 feet
00UonDSW
Number Boring NumberB-23
Date Drilling Completed
09/24/96
Surface ElevationFeet MSL
Drilling Method
HSA
Borehole Diameter7.0 Inches
Local Grid Location (If applicable)D N
Feet D SD E
Feet D WCivil Town/City/ or VillageEau Claire
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QiU14:20
14:25
14:30
14:35
I hereby certify that the information on this form is true and correct to the best of my knowledge.Signature Firm Eder Associates
8025 Excelsior Drive Madison, WI 53717Tel: (608)836-1500 Fax: (608)831-3337
This form is auy<oride6'gy/Chap^jaxi44, 147 and 162, Wis. Stats. Completion of thisjeport is mandatory. Penalties: Forfeit not less than $10 normore than $5,000 for each violation. Fined not less than $10 or more than $100 or imprisoned not less than 30 days, or both for each violation.Each day of continued violation is a separate offense, pursuant to ss 144.99 and 162.06, Wis. Stats.
State of WisconsinDepartment of Natural Resources
Route To:D Solid WasteEH Emergency Responsed Wastewater
D Haz. WasteD Underground TanksD Water ResourcesD Other
Soil Boring Log InformationForm 4400-122 7.91
Page 1 of 1Facility/Project Name License/Permit/Monilonng Number
National Presto Industries-Lagoon No. 1Boring
Boring NumberB-24
Drilled By (Firm name and name of crew chief) Date Dri l l ing Started Date Drilling CompletedBoart Longyear (Mike Mueller)
DNR Facility Well No. WI Unique Well No.
Boring LocationState PlaneSW 1/4 of SE 1/4 of Section 34
CountyChippewa
Sample
|
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Leng
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— 1
-2
-3
—4
-5
-6
-7
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09/24/96 09/24/96
Drill ing Method
HSA
Common Well Name Final Static Water Level Surface Elevation Borehole Diameter
FeetMSL Feet MSL 7.0 InchesLocal Grid Location (If applicable)
N, E Lat ° '" r-, N n £
T 28 N,R 9 W Long ° ' " Feet D S Feet D WDNR County Code9
Soil/Rock DescriptionAnd Geologic Origin For
Each Major Unit
Brown oily medium to coarse sand
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Same as above
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00Oin
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men
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14:50
14:53
14:55
15:00
I hereby certify that the information on this form is true and correct to the best of my knowledge.Signature Firm Associates
8025 Excelsior Drive Madison, WI 53717Tel: (608)836-1500 Fax: (608)831-3337
This form isZauthoTlZatfjJy CMpte/s 144, 147 and 162, Wis. Stats. Completion of this report is mandatory. Penalties: Forfeit not less than $10 normore than $5,000 for each vio+anon. Fined not less than $10 or more than $100 or imprisoned not less than 30 days, or both for each violation.Each day of continued violation is a separate offense, pursuant to ss 144.99 and 162.06, Wis. Stats.
State of WisconsinDepartment of Natural Resources
WELL/DRILLHOLE/BOREHOLE ABANDONMENTForm 3300-5W 11-89
All abandonment work shall be performed in accordance with theAdmin. Code, whichever is applicable. Also, see instructions on
provisions of Chapters NR 111, NR 112 or 141, Wis.back.
GENERAL INFORMATIONWell/Drillhole/Borehole (
Location
1/4 of 1/4 of Sen(If Applicable)
Gov't I fitGrid Location
ft. n N. n s..
\(2) FACILITY NAME PRESTO,ounty
Eau Clairen E
;T N- R. PI W
Grid Nnmhpr
ft n F n wCivil Town Name
Street Address of Well
City, Village
Chippewa Falls
Original Well Owner (It Known)
Present Well OwnerPRESTO
Street or Route
City, State, Zip CodeChippewa Falls, WI
Facility Well No. and/or Name
B-10Reason For Abandonment
Test BoringDate of Abandonment
9-19-96
[If Applicable) WI Unique Well No.
WELL/DRILLHOLE/BOREHOLE INFORMATION(3) Original Well/Drillhole/Borehole Construction Completed On
(Date)
LJ Monitoring WellD Water WellE3 Drillholen Borehole
Construction Type:K Drilled D Driven (PI Other (Specify^
Formation Type:[XJ Unconsolidated Formation
Construction Report Available?E3 Yes D No
Sandpoint) CD Dug
D Bedrock
Total Well Depth (ft) Casing Diameter Cin<; )(From groundsurface)
Casing Depth (Ft )
Was Well Annular Space Grouted?If Yes, To What Depth?
D Yes D No D UnknownFeet
(7)Sealing Material Used
Bentonite Chips
(4) Depth in Water (Feert Dry
Pump & Piping Removed? CD Yes D No ^ Not ApplicableLiner(s) Removed? D Yes CD No £3 Not ApplicableScreen Removed? D Yes D No Kl Not ApplicableCasing Left in Place? D Yes D NoIf No, F.iplain
Was Casing Cut Off Below Surface? D Yes D NoDid Sealing Material Rise to Surface? ^ Yes D NoDid Material Settle After 24 Hours? D Yes [3 NoIf Yes, Was Hole Retopped? D Yes D No
(5) Required Method of Placing Sealing MaterialE3 Conduct^ p;"e - Gravity LJ Conductor Pipe - PumpedD Dump Bailer D Other (Explain)
(6) Sealing Materials For monitoring wells andCD Neat Cement Grout monitoring well boreholes onlyCD Sand-Cement (Concrete) Grout1 1 Concrete 1 1 Bentonite PelletsCD Clay-Sand Slurry CD Granular BentoniteCD Bentonite-Sand Slurry CD Bentonite-Cement GroutE3 Chipped Bentonite
No. YarFrom (Ft.) To (Ft.) Sacks Sea
or Volut
Surface 45.0 15 B<
(9) Name of Person or Firm Doing Sealing WorkBoart Longyear
Signature of Person Doing WorkJC^tsML^.Street or Route
101 Alderson Street
Date Signed
)D-^-q^Telephone Number(715) 359-7090
City, State, Zip Code
Schofield, WI 54476
ds,lant Mix Ratio or Mud Weightne
igs
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DNR/COUNTY
State of WisconsinDepartment of Natura l Resources
Route To:D Solid WasteO Emergency ResponseD Wastewater
D Haz. Wastel~l Underground Tanksl~l Water ResourcesD Other
Soil Boring Log InformationForm 4400-122 7.91
Page 1 of 3Facility/Project Name
National Presto Industries-Lagoon No. 1Boring Drilled By (Firm name and name of crew chief)
Boart Longyear (Mike Mueller)
DNR Facility Well No. WI Unique Well No. Common Well Name
License/Permit/Monitoring
Date Drilling Started
09/19/96
Final Static Water LevelFeet MSL
Boring LocationState Plane N, ESW l / 4 o f S E 1/4 of Section 34 T 28 N,R 9 W
LatLong ° ' "
County DNR County CodeChippewa 9
Sample
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Soil/Rock DescriptionAnd Geologic Origin For
Each Major Unit
Red-brown medium to coarse sand
Same as above
Same as above
U
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Number Borine NumberB-ii
Date Drilling Completed
09/19/96
Drilling Method
HSA
Surface Elevation Borehole Diameter
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I hereby certify that the information on this form is true and correct to the best of my knowledge.Signature Firm ^der Associates
8025 Excelsior Drive Madison, WI 53717Tel: (608)836-1500 Fax: (608)831-3337
This form is authonzM by Chaffs 144, 147 and 162, Wis. Stats. Completion of this report is mandatory. Penalties: Forfeit not less than $10 normore than $5,000 for each violation. Fined not less than $10 or more than $100 or imprisoned not less than 30 days, or both for each violation.Each day of continued violation is a separate offense. pursuant to ss 144.99 and 162.06, Wis. Stats.
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State of WisconsinDepartment of Natural Resources
WELL/DRILLHOLE/BOREHOLE ABANDONMENTForm3300-5W 11-89
All abandonment work shall be performed in accordance with theAdmin. Code, whichever is applicable. Also, see instructions on
provisions of Chapters NR 111, NR 112 or 141, Wis.back.
GENERAL INFORMATIONWell/Drillhole/BoreholeLocation
1/4 of 1/4 of Sec(If Applicable)
Oov't I fitGrid Location
ft. D N. D s.,
County
Eau ClaireD E
;T. N; R. l~~l W
Orid Number
ft n F. n wCivil Town Name
Street Address of Well
City, VillageChippewa Falls
(2) FACILITY NAME PRESTOOriginal Well Owner (It Known)
Present Well OwnerPRESTO
Street or Route
City, State, Zip CodeChippewa Falls, WI
Facility Well No. and/or Name (If Applicable) WI Unique Well No.
B-llReason For Abandonment
Test BoringDate of Abandonment
9-19-96WELL/DRILLHOLE/BOREHOLE INFORMATION(3) Original Well/Drillhole/Borehole Construction Completed On
(Date)
CD Monitoring WellD Water WellS DrillholeD Borehole
Construction Type:S Drilled CD Drivenl~l Other fSpecifv}
Formation Type:S3 Unconsolidated Formation
Construction Report Available?E*3 Yes D No
(Sandpoint) 1 1 Dug
D Bedrock
Total Well Depth (ft) Casinfr Diameter (ins }(From groundsurface)
Casing Depth (Ft )
Was Well Annular Space Grouted?If Yes, To What Depth?
D Yes D No D UnknownFeet
(7)Sealing Material Used
Bentonite Chips
(4) Depth to Water (FeetPump & Piping RemcLiner(s) Removed?Screen Removed?Casing Left in Place?
j Drywed? CD Yes CD No ^ Not Applicable
CD Yes CD No ^ Not ApplicableD Yes CD No S3 Not ApplicableCD Yes CD No
Was Casing Cut Off Below Surface?Did Sealing Material Rise to Surface?Did Material Settle After 24 Hours?If Yes, Was Hole Retopped?
D Yes D NoE*3 Yes D NoCD Yes E3 NoD Yes D No
(5) Required Method of Placing Sealing MaterialS Conductor Pipe - Gravity CD Conductor Pipe - PumpedCD Dump Bailer CD Other (Explain)
(6) Sealing MaterialsCD Neat Cement GroutCD Sand-Cement (Concrete) Grout1 1 ConcreteD Clay-Sand SlurryCD Bentonite-Sand SlurryC3 Chipped Bentonite
From (Ft.) To (Ft.)
Surface 48.0
No. Yards,Sacks Sealant
or Volume
15 Bags
For monitoring wells andmonitoring well boreholes only
CD Bentonite PelletsLD Granular BentoniteCD Bentonite-Cement Grout
Mix Ratio or Mud Weight
(8) Comments
(9) Name of Person or Firm Doing Sealing WorkBoart Longyear
Street or Route101 Alderson Street
City, State, Zip CodeSchofield, WI 54476
Date Signed
Telephone Number(715) 359-7090
DNR/COUNTY
State of WisconsinDepartment of Natural Resources
Route To:D Solid WasteCD Emergency Responsel~l Wastewater
n Haz. Wastel~l Underground TanksCD Water ResourcesD Other
Soil Boring Log InformationForm 4400-122 7-91
Page 1 of 3Facility/Project Name
National Presto Industries-Lagoon No. 1Boring Drilled By (Firm name and name of crew chief)
Boart Longyear (Mike Mueller)
DNR Facility Well No. WI Unique Well No. Common Well Name
Boring LocationStateSW
Plane1/4 of SE
CountyChippewa
Sample
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License/Permit/Monitoring Number
Date Dr i l l ing Started
09/23/96
Final Static Water LevelFeet MSL
I
Lat " ' "
-ong ° ' "DNR County Code9
H.uQ
-1
-2
-3
-4
-5
-6
-7
-8
-9
-10
-11
-12
Soil/Rock DescriptionAnd Geologic Origin For
Each Major Unit
Black medium to coarse sand with blacktar-like substance
Brown medium to coarse sand
Same as above
00UV)DSW
Boring NumberB-12A
Date Drill ing Completed
09/23/96
Surface ElevationFeet MSL
Drilling Method
HSA
Borehole Diameter7.0 Inches
Local Grid Location (If applicable)D N
Feet D SD E
Feet D WCivil Town/City/ or VillageEau Claire
o
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13:40
13:50
I hereby certify that the information on this form is true and correct to the best of my knowledge.Signature Firm £(jer Associates
8025 Excelsior Drive Madison, WI 53717Tel: (608)836-1500 Fax: (608)831-3337
This form is aVthori^edVrjy Chapters 144, 147 and 162, Wis. Stats. Completion of this report is mandatory. Penalties: Forfeit not less than $10 normore than $5,000 for each violation. Fined not less than $10 or more than $100 or imprisoned not less than 30 days, or both for each violationEach day of continued violation is a separate offense, pursuant to ss 144.99 and 162.06, Wis. Stats.
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State of WisconsinDepartment of Natural Resources
WELL/DRILLHOLE/BOREHOLE ABANDONMENTForm3300-5W H-gg
All abandonment work shall be performed in accordance with theAdmin. Code, whichever is applicable. Also, see instructions on
provisions of Chapters NR 111, NR 112 or 141, Wis.back.
A GENERAL INFORMATIONWell/Drillhole/Borehole CountyLocation Eau Claire
D E1/4 of 1/4 of Sec. ;T N- R H W
(If Applicable)
fiov't I,ot Grid NumberGrid Location
ft. D N. D S., ft. D E. D W.Civil Town Name
Street Address of Well
City, Village
Chippewa Falls
(2) FACILITY NAME PRESTOOriginal Well Owner (U Known}
Present Well Owner
PRESTOStreet or Route
City, State, Zip CodeChippewa Falls, WI
Facility Well No. and/or Name
B-12AReason For Abandonment
Test BoringDate of Abandonment
9-23-96
(If Applicable) WI Unique Well No.
WELL/DRILLHOLE/BOREHOLE INFORMATION(3) Original Well/Drillhole/Borehole Construction Completed On
(Date)
LJ Monitoring Well Construction Report Available?CD Water Well El Yes D NoEl DrillholeD Borehole
Construction Type:El Drilled G Driven (Sandpoint) CD Dug[~l Other (Specify^
Formation Type:L*J om.ui.oOHdated Formation LJ Bedrock
Total Well Depth (ft) Casing Diameter Cinsl(From groundsurface)
Casing Depth CFtl
Was Well Annular Space Grouted? D Yes D No D UnknownIf Y« , To What Depth'' Feet
(7)Sealing Material Used
Bentonite Chips
(4) Depth to Water (Feet) P^YPump & Piping Removed?Liner(s) Removed?Screen Removed?Casing Left in Place?If No, Explain
CD Yes CD No E] Not ApplicableCD Yes D No El Not ApplicableCD Yes CD No E] Not ApplicableCD Yes CD No
Was Casing Cut Off Below Surface? D Yes D NoDid Sealing Material Rise to Surface? E] Yes [H NoDid Material Settle After 24 Hours? D Yes El NoIf Yes, Was Hole Retopped? D Yes D No
(5) Required Method of Placing Sealing MaterialEl Conductor Pipe - Gravity CD Conductor Pipe - PumpedD Dump Bailer D Other (Explain)
(6) Sealing Materials For monitoring wells andCD Neat Cement Grout monitoring well boreholes only1 1 Sand-Cement (Concrete) Grout1 1 Concrete CD Bentonite Pellets1 1 Clay-Sand Slurry CD Granular BentoniteCD Bentonite-Sand Slurry CD Bentonite-Cement Groutl*J Chipped Bentonite
No. YaFrom (Ft.) To (Ft.) Sacks Se
or Volu
Surface 41.0 12 B
rds,alant Mix Ratio or Mud Weightme
ags
(9) Name of Person or Firm Doing Sealing WorkBoart Longyear
Signature ^erson Qoitu Work
Street or Route101 Alderson Street
Date Signed
JO-3-%,Telephone Number
(715) 359-7090City, State, Zip Code
Schofieid, WI 54476
mM^M-yfm&m^,Ss
R
&
viKwrtlKs^EKkir
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.':
DNR/COUNTY
State of WisconsinDepartment of Natural Resources
Route To:D Solid WasteCD Emergency Responsen Wastewater
D Haz. WasteC] Underground Tanksl~l Water ResourcesD Other
Soil Boring Log InformationForm 4400-122 7-91
Page 1 of 3Facility/Project Name License/Permit/Monitoring Number
National Presto Industries-Lagoon No. 1Boring NumberB-13
Boring Drilled By (Firm name and name of crew chief) Date Dril l ing Started Date Dri l l ing CompletedBoart Longyear (Mike Mueller)
DNR Facility Well No. WI Unique Well No.
Boring LocationState Planesw 1/4 of SE 1/4 of Section 34
CountyChippewa
Sample
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-8
-9
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-12
09/23/96 09/23/96
Common Well Name Final Static Water Level Surface ElevationFeet MSL Feet MSL
Drilling Method
HSA
Borehole Diameter7.0 Inches
Local Grid Location (If applicable)N, ET 28 N . R 9 W 1
T of " ' "Ut D N.ong ° ' " Feet D S
DNR County Code9
Soil/Rock DescriptionAnd Geologic Origin For
Each Major Unit
Black medium to coarse sand
Brown medium to
Same as above
coarse sand
GOUGODSW
Civil Town/City/ or VillageEau Claire
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16:05
16:10
I hereby certify that the information on this form is true and correct to the best of my knowledge.Signature Firm g^er Associates
8025 Excelsior Drive Madison, WI 53717Tel: (608)836-1500 Fax: (608)831-3337
This form is^jthofi^iecttfy Chapt/rs L44, 147 and 162, Wis. Stats. Completion of this report is mandatory. Penalties: Forfeit not less than $10 normore than $5,000 for each violatrorh Fined not less than $10 or more than $100 or imprisoned not less than 30 days, or both for each violation.Each day of continued violation is a separate offense, pursuant to ss 144 99 and 162.06, Wis. Stats.
M Ko
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State of WisconsinDepartment of Natural Resources
WELL/DRILLHOLE/BOREHOLE ABANDONMENTForm3300-5W H.g9
All abandonment work shall be performed in accordance with theAdmin. Code, whichever is applicable. Also, see instructions on
provisions of Chapters NR 111, NR 112 or 141, Wis.back.
GENERAL INFORMATIONWell/Drillhole/BoreholeLocation
1/4 of 1/4 of Sec(If Applicable)
Cmv't I .orGrid Location
ft n N n s
County
Eau Clairen E
; T. N; R l~~l W
Grid Number
ft n F n wCivil Town Name
Street Address of Well
City, VillageChippewa Falls
(2) FACILITY NAME PRESTOOriginal Well Owner (If Known)
Present Well OwnerPRESTO
Street or Route
City, State, Zip CodeChippewa Falls, WI
Facility Well No. and/or Name
B-13Reason For Abandonment
Test BoringDate of Abandonment
9-23-96
(If Applicable) WI Unique Well No.
WELL/DRILLHOLE/BOREHOLE INFORMATION(3) Original Well/Drillhole/Borehole Construction Completed On
(Date)
CD Monitoring WellD Water WellE3 DrillholeCD Borehole
Construction Type:E3 Drilled D DrivenPI Other (Specify)
Formation Type:^ Unconsolidated Formation
Construction Report Available?(El Yes D No
(Sandpoint) CD Dug
D Bedrock
Total Well Depth rft) Casino Diamprpr Cin« ^(From groundsurface)
Casing Depth fFt )
Was Well Annular Space Grouted?If Yes, To What Depth?
D Yes D No D UnknownFeet
(7)Sealing Material Used
Bentonite Chips
(4) Di-pth fn Water (Feel) 43.0
Pump & Piping Removed?Liner(s) Removed?Screen Removed?Casing Left in Place?If Nn, Explain
D Yes D No S Not ApplicableD Yes D No S Not ApplicableD Yes D No ^ Not ApplicableD Yes D No
Was Casing Cut Off Below Surface? D Yes D NoDid Sealing Material Rise to Surface? S Yes l~~1 NoDid Material Settle After 24 Hours? D Yes K NoIf Yes, Was Hole Retopped? D Yes D No
(5) Required Method of Placing Sealing MaterialH Conductor Pipe - Gravity CD Conductor Pipe - PumpedD Dump Bailer CD Other (Explain)
(6) Sealing Materials For monitoring wells andCD Neat Cement Grout monitoring well boreholes onlyD Sand-Cement (Concrete) GroutCD Concrete CD Bentonite PelletsD Clay-Sand Slurry CD Granular BentoniteCD Bentonite-Sand Slurry CD Bentonite-Cement GroutS Chipped Bentonite
No. YaFrom (Ft.) To (Ft.) Sacks Se
or Volu
Surface 43.0 15 B
rds.alant Mix Ratio or Mud Weightme
ags
(8) Comments
(9) Name of Person or Firm Doing Sealing WorkBoart Longyear
Signature of Person Doing Work
Street or Route —101 Alderson Street
Date Signed
JO- 3- 9lpTelephone Number(715) 359-7090
City, State, Zip Code
Schofield, WI 54476
fl$£:::::::::::::::x::FW;pNfcpK<
ffilllSII I
^Qywvys£<jNL.Y: DxsKiel/CoMrt*" <:
DNR/COUNTY
State of WisconsinDepartment of Natural Resources
Route To:n Solid WasteCH Emergency Response[~l Wastewater
D HHZ. Waster~l Underground Tanksl~l Water ResourcesD Other
Soil Boring Log InformationForm 4400-122 7-91
Page 1 of 3Facility/Project Name
National Presto Industries-Lagoon No. 1Boring Drilled By (Firm name and name ot crew chief)
Boart Longyear (Mike Mueller)
DNR Facility Well No.
Boring LocationState PlaneSW 1/4 of SE
CountyChippewa
Sample
J
'
11
Leng
th (
in)
Reco
vere
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20
16
ts>asoUo
CO1124
3479
25711
ILU-
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-1
_ 2
-3
-4
-5
" 6
—7
1 O
-9
WI Unique Well No. Common Well Name
N, E1/4 of Section 34 T 28 N . R 9 W
License/Permit/Monitoring
Date Dri l l ing Started
09/19/96
Final Static Water LevelFeet MSL
Lat ° ' "
Long ° ' "DNR County Code9
-10
— 1-
— 12
Soil/Rock DescriptionAnd Geologic Origin For
Each Major Unit
Brown medium to coarse sand
Same as above
Same as above
00
U00
SW
Number Boring NumberB-14
Date Dri l l ing Completed
09/19/96
Drill ing Method
HSA
Surface Elevation Borehole DiameterFeet MSL 7.0 Inches
Local Grid Location (If applicable)D N D E
Feet D S Feet D WCivil Town/City/ or VillageEau Claire
o'js«" 00u. oo J3
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/FID
Soil Properties
Stan
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oist
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Cont
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M
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15:35
15:45
15:50
I hereby certify that the information on this form is true and correct to the best of my knowledge.Signature Firm £({er Associates
8025 Excelsior Drive Madison, WI 53717Tel: (608)836-1500 Fax: (608)831-3337
This form is auuiorizewpy ChapferJ3H4, 147 and 162, Wis. Stats. Completion of this report is mandatory. Penalties: Forfeit not less than $10 normore than S5.000 for each violwton. Fined not less than SIO or more than $100 or imprisoned not less than 30 days, or both for each violation.Each day of continued violation is a separate offense. pursuant to ss 144.99 and 162.06, Wis. Stats.
State of WisconsinDepartment of Natural Resources
Soil Boring Log Information SupplementForm4400-122A 7-91
Boring Number B-14 Use only as an attachment to Form 4400-122. Page 2 of 3Sample
Num
ber
Leng
th (
in)
Reco
vere
d
1 21
• 23
• 2211
J
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C0u0
CQ5566
5
91213
9121216
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-15
h-16
-17
-18
-19
-20
-21
-22
-23
-24
-25
-26
-27
-28
-29
-30
.
-31
-32
Soil/Rock DescriptionAnd Geologic Origin For
Each Major Unit
Same as above
Same as above
COUCO
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5.3X*X*>***^>&**.*":|:|:|:|X*X*•I**.****.jjjijij*********;£>**X**
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k k kk k k k
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k % k kk k k k
k k k k
k k k kk k k kk k k kk k k kk k k kk k k kk k k kk k k kk k k k
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= 1(JJ Cfl
£5 PID
/FID
Soil Properties
Stan
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Pene
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onten
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Blow Counts
Depth In Feet
Isi?s lB- O o2 0 G.
Cro ~£. o a•1 O 8it!-•-• 3 C.
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StandardPenetrationMoistureContentLiquidLimitPlasticLimit
P200
RQD/Comments
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Stale of WisconsinDepartment of Natural Resources
WELL/DRILLHOLE/BOREHOLE ABANDONMENTForm 3300-5W 11-89
All abandonment work shall be performed in accordance with theAdmin. Code, whichever is applicable. Also, see instructions on
provisions of Chapters NR 111, NR 112 or 141, Wisback.
GENERAL INFORMATIONWell/Drillhole/BoreholeLocation
1/4 of 1/4 of Sec(If Applicable)
Gov't InrGrid Location
ft n N. n s
County
Eau ClaireD E
; T N; R D W
Grid Number
ft n R n wCivil Town Name
Street Address of Well
City, Village
Chippewa Falls
(2) FACILITY NAME PRESTOOriginal Well Owner (If Known)
Present Well Owner
PRESTOStreet or Route
City, State, Zip CodeChippewa Falls, WI
Facility Well No. and/or Name (If Applicable) WI Unique Well No.
B-14Reason For Abandonment
Test BoringDate of Abandonment
9-19-96WELL/DRILLHOLE/BOREHOLE INFORMATION(3) Original Well/Drillhole/Borehole Construction Completed On
(Date)
LJ Monitoring WellCH Water Well§3 DrillholeD Borehole
Construction Type:E3 Drilled D DrivenPI Other (Specify)
Formation Tvpe:C*J Uncoiiiol idated Formation
Construction Report Available?S Yes D No
(Sandpoint) LJ Dug
D Bedrock
Total Well Depth (ft) Casing Diameter (ins />(From groundsurface)
Casing Depth (Ft )
Was Well Annular Space Grouted?If Yes, To What Depth?
D Yes D No D UnknownFeet
(7)Sealing Material Used
Bentonite Chips
(4) Depth to Water (FeetPump & Piping RemcLiner(s) Removed?Screen Removed?Casing Left in Place?If No, Explain
> Dry>ved? D Yes D No ED Not Applicable
D Yes D No S Not ApplicableD Yes D No S3 Not ApplicableD Yes D No
Was Casing Cut Off Below Surface?Did Sealing Material Rise to Surface?Did Material Settle After 24 Hours?If Yes, Was Hole Retopped?
D Yes D NoE Yes D NoD Yes ^ NoD Yes D No
(5) Required Method of Placing Sealing MaterialE*J Conductor Pipe - Gravity 1 1 Conductor Pipe - PumpedD Dump Bailer d Other (Explain)
(6) Sealing MaterialsLJ Neat Cement GroutCH Sand-Cement (Concrete) GroutLJ ConcreteD Clay-Sand SlurryLJ Bemonile-Sand Slurry^ Chipped Bentonite
From (Ft.) To (Ft.)
Surface 39.5
No. Yards.Sacks Sealant
or Volume
14 Bags
For monitoring wells andmonitoring well boreholes only
L~D Bentonite PelletsLJ Granular Bentonited Bentonite-Cement Grout
Mix Ratio or Mud Weight
(9) Name of Person or Firm Doing Sealing Work
Boart LongyearSignature of Person Doing Work
SreeTor Rd^ite ^"^ "" —101 Alderson Street
Date Signed
IO-3-9UTelephone Number
(715) 359-7090City, State. Zip Code
Schofield, WI 54476
f4D~
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fc^:-:-tt-&>K&faie:3l:ecelve<HtrtSptt3fct
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?.l&RimXm-m-&:+<<:-IDiSKl 2/GtJHJH <••••
DNR/COUNTY
State of WisconsinDepartment of Natural Resources
Route To:D Solid Waste[D Emergency Responsel~l Wastewater
D Haz. WasteC3 Underground Tanksl~l Water ResourcesD Other
Soil Boring Log InformationForm 4400-122 7-91
Page 1 of 3Facility/Project Name License/ Permit/Monitoring Number
National Presto Industries-Lagoon No. 1Boring NumberB-15A
Boring Drilled By (Firm name and name of crew chief) Date Dr i l l i ng Started Date Dri l l ing CompletedBoart Longyear (Mike Mueller)
DNR Facility Well No. WI Unique Well No.
Boring LocationState PlaneSW 1/4 of SE 1/4 of Section 34
CountyChippewa
Sample
Num
ber
I
|-
1-
Leng
th (
in)
Reco
vere
d
I -
r
C/J
c
(3o
calll7
3768
3456
i;U,
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.--1
-2
-3
—4
-5
-6
-7
-8
-9
-10
— 11
-12
09/23/96 09/23/96
Drilling Method
HSA
Common Well Name Final Static Water Level Surface Elevation Borehole Diameter
Feet MSL Feet MSL 7.0 InchesLocal Grid Location (If applicable)
N, E Lat ° ' " n N PI FT 28 N.R 9 W Long ° ' " Feet D S Feet D W
DNR County Code9
Soil/Rock DescriptionAnd Geologic Origin For
Each Major Unit
Dark brown medium to coarse sand withfew fine gravel
Brown medium to
Same as above
coarse sand
onUC/5
SW
Civil Town/City/ or VillageEau Claire
oIS«• ooi-, o0-J
! >Xf. v.": W. >,v: WI >Xf» *x*.. v/> %v> v/>% %
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Stan
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Pene
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oistu
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t
M
M
M
-o
11
U
to 'c_£3 C
8<ND. RQ
D/Co
mm
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10:45
11:00
11:10
I hereby cenify that the information on this form is true and correct to the best of my knowledge.Signature Firm Associates
8025 Excelsior Drive Madison, WI 53717Tel: (608)836-1500 Fax: (608)831-3337
This form is authori££d/by Chapren 144, 147 and 162, Wis. Stats. Completion of this report is mandatory. Penalties: Forfeit not less than $10 normore than $5,000 for each vbfcftion. Fined not less than $10 or more than $100 or imprisoned not less than 30 days, or both for each violationEach day of continued violation is a separate offense, pursuant to ss 144 99 and 162 06, Wis Stats.
State of WisconsinDepartment of Natural Resources
Soil Boring Log Information SupplementForm 4400-122A 7-91
Boring Number B-15A Use only as an attachment to Form 4400-122. Page 2 of 3Sample
Num
ber
Leng
th (
in)
Reco
vere
d
• 22!
21
Blow
Cou
nts
3
61010
6
1315
5UH
C
ex<UQ
-13
-14
-15
-16
-17
-18
-19
-20
-21
-22
-23
-24
-25
-26
-27
-28
-29
-30
-31•
-32
Soil/Rock DescriptionAnd Geologic Origin For
Each Major Unit
Same as above
Same as above
00O00D
CUeO W>o2
Si-!
1r%%%£
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fc fc fc kk k fc k
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— s?£5 PID
/FID
Soil Properties
Stan
dard
Pene
tratio
nM
oist
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Cont
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M
M
"2 ~ 0 ^
to 'cm cO. J
8CNCU RQ
D/Co
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ents
11:20
11:30
DO piB 2W 03
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1 \ 1 \ ".
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dumber
Length (in)Recovered
Blow Counts
Depth In Feet
£ « «D. 0
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u s e sGraphicLogWellDiagram
PID/FID
StandardPenetrationMoistureContentLiquidLimitPlasticLimit
P200
RQD/Comments
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State of WisconsinDepartment of Natural Resources
WELL/DRILLHOLE/BOREHOLE ABANDONMENTForm 3300-5W H.gg
All abandonment work shall be performed in accordance with theAdmin. Code, whichever is applicable. Also, see instructions on
provisions of Chapters NR 111, NR 112 or 141, Wis.back.
) GENERAL INFORMATIONWell/Drillhole/BoreholeLocation
1/4 of 1/4 of Sec.(If Applicable)
Oov't LotGrid Location
ft n N n s
County
Eau ClaireD E
; T N; R Fl W
find Number
ft n R n wCivil Town Name
Street Address of Well
City, VillageChippewa Falls
(2) FACILITY NAME PRESTOOriginal Well Owner (If Known)
Present Well OwnerPRESTO
Street or Route
City, State, Zip CodeChippewa Falls, WI
Facility Well No. and/or Name
B-15A(If Applicable) WI Unique Well No.
Reason For AbandonmentTest Boring
Date of Abandonment
9-23-96WELL/DRILLHOLE/BOREHOLE INFORMATION(3) Original Well/Drillhole/Borehole Construction Completed On
(Date)
CD Monitoring WellD Water WellE3 DrillholeD Borehole
Construction Type:G3 Drilled D Driven(~1 Other (Spcrify)
Formation Type:E3 Unconsolidated Formation
Construction Report Available?[3 Yes D No
(Sandpoint) LJ Dug
D Bedrock
Tn'a.1 Well FVprh (ft) Casinp Diameter (ins 1(From groundsurface)
Hating Depth (Ft )
Was Well Annular Space Grouted?If Yes, To What Depth?
D Yes D No D UnknownFeet
(7) Sealing Material Used
Bentonite Chips
(4) Depth to Water (Feet) PryPump & Piping Removed?Liner(s) Removed?Screen Removed?Casing Left in Place?If No, F.iplain
D Yes D No ^ Not ApplicableD Yes D No S Not ApplicableLI Yes D No S Not ApplicableD Yes D No
Was Casing Cut Off Below Surface? D Yes D NoDid Sealing Material Rise to Surface? [3 Yes D NoDid Material Settle After 24 Hours? D Yes ^ NoIf Yes, Was Hole Retopped? D Yes D No
(5) Required Method of Placing Sealing MaterialS Conductor Pipe - Gravity LJ Conductor Pipe - PumpedD Dump Bailer C3 Other (Explain)
(6) Sealing Materials For monitoring wells and1 1 Neat Cement Grout monitoring well boreholes onlyCH Sand-Cement (Concrete) GroutLJ Concrete LJ Bentonite PelletsLJ Clay-Sand Slurry LJ Granular Bentonite1 1 Bentonite-Sand Slurry 1 1 Bemonite-Cement Grout^ Chipped Bentonite
No. YaFrom (Ft.) To (Ft.) Sacks Se
or Vok
Surface 38.5 11 B
rds,alant Mix Ratio or Mud Weightime
ags
(8) Comments
(9) Name of Person or Firm Doing Sealing WorkBoart Longyear
Sijyature of Person Doing WorkSiaiature or Persi
/t———S iStreet or Route101 Alderson Street
Date Signed
Telephone Number(715) 359-7090
City, State, Zip Code
Schofield, WI 54476DNR/COUNTY
State of WisconsinDepartment of Natural Resources
Route To:D Solid WasteCl Emergency ResponseCD Wastewater
D Haz. Wastel~l Underground TanksE] Water ResourcesD Other
Soil Boring Log InformationForm 4400-122 7.91
Page 1 of 3Facility/Project Name
National Presto Industries-Lagoon No. 1Boring Drilled By (Firm name and name of crew chief)
Boart Longyear (Mike Mueller)
DNR Facility Well No.
Boring LocationState PlaneSW 1/4 of SE
CountyChippewa
Sample
Num
ber
!
|I1
\tm
Leng
th (i
n)Re
cove
red
14
19
19
CAS
0QQ1244
5101013
3557
57913
WI Unique Well No. Common Well Name
N, E1/4 of Section 34 T 28 N.R 9 W
License/Permit/Monitoring
Date Drilling Started
09/24/96
Final Static Water LevelFeet MSL
I
Lat ° ' "
-xmg ° ' "DNR County Code9
1JC
a.Q
-1
—2
-3
-4
-5
-6
-7
H8•
-9
-10
-1
-12
Soil/Rock DescriptionAnd Geologic Origin For
Each Major Unit
Brown medium to coarse sand
Same as above with some fine gravel
Same as above
c/nUtO
SW
Number Boring NumberB-16
Date Dril l ing Completed
09/24/96
Surface ElevationFeet MSL
Dri l l ing Method
HSA
Borehole Diameter7.0 Inches
Local Grid Location (If applicable)n N n E
Feet D S Feet D WCivil Town/City/ or VillageEau Claire
o
f MUi Q0 J
Ir f r r if r p r •f w f rf r r r i
r r f rr r f r I
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Stan
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8:10
8:15
8:20
8:30
I hereby certify that the information on this form is true and correct to the best of my knowledge.Signature Firm Eder Associates
8025 Excelsior Drive Madison, WI 53717Tel: (608)836-1500 Fax: (608)831-3337
This form is auth6f/ized'#^,(2naptej^J^C 147 and 162, Wis. Stats. Completion of this report is mandatory. Penalties: Forfeit not less than $10 normore than $5,000 for each violatioir Fined not less than $10 or more than $100 or imprisoned not less than 30 days, or both for each violation.Each day of continued violation is a separate offense. pursuant to ss 144.99 and 162.06, Wis. Stats.
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State of WisconsinDepartment of Natural Resources
WELL/DRILLHOLE/BOREHOLE ABANDONMENTForm3300-5W H.gg
All abandonment work shall be performed in accordance with theAdmin. Code, whichever is applicable. Also, see instructions on
provisions of Chapters NR 111, NR 112 or 141, Wis.back.
GENERAL INFORMATIONWell/Drillhole/BoreholeLocation
1/4 of 1/4 of Sec.(If Applicable)
Gov't I sitGrid Location
ft n N n s
County
Eau ClaireD E
;T N; R. CD W
Grid Number
f, n P n wCivil Town Name
Street Address of Well
City, Village
Chippewa Falls
(2) FACILITY NAME PRESTOOriginal Vvell Owner (If Known;
Present Well Owner
PRESTOStreet or Route
City, State, Zip CodeChippewa Falls, WI
Facility Well No. and/or Name
B-16Reason For Abandonment
Test BoringDate of Abandonment
9-24-96
(If Applicable) WI Unique Well No.
WELL/DRILLHOLE/BOREHOLE INFORMATION(3) Original Well/Drillhole/Borehole Construction Completed On
(Date) . . . .
CD Monitoring WellD Water WellS DrillholeCD Borehole
Construction Type:S Drilled D DrivenPI Other (Specify^
r '- "".-fie:^ Unconsolidated Formation
Construction Report Available?El Yes D No
(Sandpoint) CD Dug
D Bedrock
Total Well Depth (ftl Casine Diameter lin.O(From groundsurface)
Casing Dpprh (Ft )
Was Well Annular Space Grouted?If Yes, To What Depth?
D Yes D No D UnknownFee.
(7)Sealing Material Used
Bentonite Chips
(4) Depth to Water (Feet) PryPump & Piping Removed?Liner(s) Removed?Screen Removed?Casing Left in Place?Tf Nn, Fiplain
D Yes D No S Not ApplicableD Yes D No S Not ApplicableD Yes n No ^ Not ApplicableD Yes D No
Was Casing Cut Off Below Surface? D Yes D NoDid Sealing Material Rise to Surface? S Yes D NoDid Material Settle After 24 Hours? D Yes E3 NoIf Yes, Was Hole Retopped? D Yes D No
(5) Required Method of Placing Sealing MaterialW Conductor Pipe - Gravity 1 1 Conductor Pipe - PumpedCD Dump Bailer CD Other (Explain)
(6) Sealing Materials For monitoring wells andCD Neat Cement Grout monitoring well boreholes onlyCD Sand-Cement (Concrete GroutCD Concrete ', CD Bentonite Pellets1 1 Clay-Sand Slurry ' CD Granular BentoniteCD Bentonite-Sand Slurry CD Bentonite-Cement Groutl*J Chipped Bentonite
No. YaFrom (Ft.) To (Ft.) Sacks Se
or Volu
Surface 42.0 14 B
rds,alant Mix Ratio or Mud Weightme
ags
(9) Name of Person or Firm Doing Sealing WorkBoart Longyear
Signature of Peqon Doins Work
ft — / i^f^U^Street or Route101 Alderson Street
Date Signed
IO-^-^CPTelephone Number
(715) 359-7090City, State, Zip Code
Schofield, WI 54476
'^^MtfmimDateiR^Si^trtsp^
Ri:yJDi^yHSpRc3k)r: :
RfllfctK:kp:N"ecessary
iti? £>lt£QWtr£:W&fi®&# ::
EiisiftojCttiriOf- :
'•':
DMR/rOTTNTY
State of WisconsinDepartment of Natural Resources
Route To:D Solid Wasten Emergency Responsen Wastewater
n Haz. Wastel~l Underground Tanks[~l Water ResourcesD Other
Soil Boring Log InformationForm 4400-122 7-91
Page 1 of 3Facility/Project Name License/Permit/Monitoring Number
National Presto Industries-Lagoon No. 1Boring NumberB-17
Boring Drilled By (Firm name and name of crew chiet) Date Drilling Started Date Dril l ing CompletedBoart Longyear (Mike Mueller) 09/24/96 09/24/96
DNR Facility Well No. WI Unique Well No. Common Well Name Final Static Water Level Surface Elevation BFeet MSL Feet MSL
Drilling Method
HSA
orehole Diameter7.0 Inches
Boring Location Local Grid Location (If applicable)State Plane N, E Lat ° ' " j-j N |-| £
SW l / 4 o f S W 1/4 of Section 34 T 28 N . R 9 W Long °'" Feet D S Feet D WCounty DNR County Code
Chippewa 9Sample
Num
ber
1
1
I
Leng
th (
in)
Reco
vere
d
18
„
eoUo
CQ1157
4
89
3878
u
H.UQ
-1
-2
-3
-4
-5
-6
—7
-9
-10
:— n
-12
Soil/Rock DescriptionAnd Geologic Origin For
Each Major Unit
Brown medium to coarse sand
Same as above
Same as above, few fine gravel
COUCODSW
Civil Town/City/ or VillageEau Claire
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M
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10:00
10:10
10:15
I hereby certify that the information on this form is true and correct to the best of my knowledge.Signature Firm E<jer Associates
8025 Excelsior Drive Madison, WI 53717Tel: (608)836-1500 Fax: (608)831-3337
This form is6^uth<#ik&i/fjy Cha{<S?rl44, 147 and 162, Wis. Stats. Completion of this report is mandatory. Penalties: Forfeit not less than $10 normore than $5,000 for each violation. Fined not less than $10 or more than $100 or imprisoned not less than 30 days, or both for each violationEach day of continued violation is a separate offcnse, pursuant to ss 144.99 and 162.06, Wis. Stats.
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State of WisconsinDepartment of Natural Resources
All abandonment work shall be performed in accordance with theAdmin. Code, whichever is applicable. Also, see instructions on
WELL/DRILLHOLE/BOREHOLE ABANDONMENTForm3300-5W ij .gg
provisions of Chapters NR 111, NR 112 or 141, Wis.back.
GENERAL INFORMATIONWell/Drillhole/Borehole CountyLocation Eau ciaire
D E1/4 of 1/4 of Sec ;T. N; R Fl W
(If Applicable)
finv'r I.ot Grid NumberGrid Location
ft n N n s ft n F n wCivil Town Name
Street Address of Well
City, VillageChippewa Falls
(2) FACILITY NAME PRESTOOriginal Well Owner (It Known;
Present Well Owner
PRESTOStreet or Route
City, State, Zip Code
Chippewa Falls, WIFacility Well No. and/or Name (If Applicable) WI Unique Well No.
B-17Reason For Abandonment
Test BoringDate of Abandonment
9-24-96WELL/DRILLHOLE/BOREHOLE INFORMATION(3) Original Well/Drillhole/Borehole Construction Completed On
fDate)
D Monitoring WellD Water WellS DrillholeCD Borehole
Construction Type:S Drilled CD DrivenPI Other fSpecify^
Formation Type:E*J Unconsolidated Formation
Construction Report Available?£3 Yes D No
(Sandpoint) CD Dug
D Bedrock
Total Well Depth (ft) Casinc Diameter f i n s 1(From ground surface)
Casing Depth fFi 1
Was Well Annular Space Grouted?If Yes, To What Depth?
D Yes D No CD UnknownFeet
(7)Sealing Material Used
Bentonite Chips
(4) Depth tPump &Liner(s'ScreenCasingIf No, E
1 Water (Feert Dry
Piping Removed? CD Yes CD No S Not ApplicableRemoved? CD Yes CD No ^ Not Applicable
Removed? CD Yes CD No 13 Not ApplicableLeft in Place? CD Yes CD Noxplain
Was Casing Cut Off Below Surface?Did Sealing Material Rise to Surface?Did Material Settle After 24 Hours?If Yes, Was Hole Retopped?
D Yes D NoK Yes D NoD Yes ^ NoD Yes D No
(5) Required Method of Placing Sealing Material^ Conductor Pipe - Gravity CD Conductor Pipe - PumpedD Dump Bailer CD Other (Explain)
(6) Sealing MaterialsCD Neat Cement GroutCD Sand-Cement (Concrete) GroutCD ConcreteD Clay-Sand SlurryCD Bentonite-Sand SlurryM Chipped Bentonite
From (Ft.)
Surface
No. Yards,To (Ft.) Sacks Sealant
or Volume
35.0 10 Bags
For monitoring wells andmonitoring well boreholes only
CD Bentonite PelletsCD Granular BentoniteCD Bentonite-Cement Grout
Mix Ratio or Mud Weight
(8) Comments
(9) Name of Person or Firm Doing Sealing WorkBoart Longyear
Street or Route101 Alderson Street
City, State, Zip Code
Schofield, WI 54476
Telephone Number(715)359-7090
State of WisconsinDepartment of Natural Resources
Route To:D Solid WasteC] Emergency Responsel~l Wastewater
D Haz. Wastel~l Underground Tanksn Water ResourcesD Other
Soil Boring Log InformationForm 4400-122 7-91
Page 1 of 3Facility /Project Name License/Permit/Monitoring Number
National Presto Industries-Lagoon No. 1Boring NumberB-18B
Boring Drilled By (Firm name and name ot crew chief) Date Drilling Started Date Drilling CompletedBoart Longyear (Mike Mueller)
DNR Facility Well No. WI Unique Well No.
Boring LocationState PlaneSW 1/4 of SW 1/4 of Section 34
CountyChippewa
Sample
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-2
— 3
—4
-5
-6
—7
— 8
-9
-10
-11
-12
09/24/96 09/24/96
Drilling Method
HSA
Common Well Name Final Static Water Level Surface Elevation Borehole Diameter
Feet MSL Feet MSL 7.0 InchesLocal Grid Location (If applicable)
N' E Lat fj N Q E
T 28 N,R 9 W Long ° ' " Feet Q S Feet D WDNR County Code9
Soil/Rock DescriptionAnd Geologic Origin For
Each Major Unit
Black medium to coarse sand with littlefine gravelBrown medium to
Same as above
Same as above
coarse sand
ooU00
DSW
Civil Town/City/ or VillageEau Claire
o
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Stan
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Pene
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Cont
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M
M
M
M
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10. RQ
D/Co
mm
ents
11:45
11:55
12:05
12:10
I hereby certify that the information on this form is true and correct to the best of my knowledge.Signature Firm E<jer Associates
8025 Excelsior Drive Madison, WI 53717Tel: (608)836-1500 Fax: (608)831-3337
This form is a<ithoj/ii(($/f>y Chapjfrrs 144, 147 and 162, Wis. Stats. Completion of this report is mandatory. Penalties: Forfeit not less than $10 normore than $5,000 for each violation. Fined not less than $10 or more than $100 or imprisoned not less than 30 days, or both for each violation.Each day of continued violation is a separate offense, pursuant to ss 144.99 and 162.06, Wis. Stats.
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State of WisconsinDepanment of Natural Resources
Soil Boring Log Information SupplementForm4400-122A 7-91
Boring Number B-18B Use only as an attachment to Form 4400-122. Page 3 of 3Sample
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Soil/Rock DescriptionAnd Geologic Origin For
Each Major Unit
Fine to medium grained sandstoneEOB @ 39 feetBackfilled with bentonite pellets
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Slate of WisconsinDepartment of Natural Resources
WELL/DRILLHOLE/BOREHOLE ABANDONMENTForm3300-5W U.g9
All abandonment work shall be performed in accordance with theAdmin. Code, whichever is applicable. Also, see instructions on
provisions of Chapters NR 111, NR 112 or 141, Wis.back.
GENERAL INFORMATIONWell/Drillhole/Borehole CountyLocation £,„ Qajre
D El / 4o f l/4of.Sec ; T N; R. flw
(If Applicable)
Oov't I.ot Grid NumberGrid Location
ft n N n s ft. n F. n wCivil Town Name
Street Address of Well
City, Village
Chippewa Falls
(2) FACILITY NAME PRESTOOriginal Well Owner (li Known)
Present Well OwnerPRESTO
Street or Route
City, State, Zip CodeChippewa Falls, WI
Facility Well No. and/or Name
B-18BReason For Abandonment
Test Boring
(If Applicable) WI Unique Well No.
Date of Abandonment9-24-96
WELL/DRILLHOLE/BOREHOLE INFORMATION(3) Original Well/Drillhole/Borehole Construction Completed On
(Date)
CD Monitoring Well Construction Report Available?D Water Well E3 Yes D NoS3 DrillholeD Borehole
Construction Type:^ Drilled D Driven (Sandpoint) CD Dug[~1 Other (Specify}
Formation "^vne:^ Unconsolidated Formation CD Bedrock
Total Well Depth (fi) Casing Diameter f ins )(From groundsurface)
Casing Depth (Ft.1
Was Well Annular Space Grouted? D Yes D No D UnknownIf Y« To What Depth1) Feet
(7)Sealing Material Used
Bentonite Chips
(4) Depth in Water (Feetl Dry
Pump & Piping Removed?Liner(s) Removed?Screen Removed?Casing Left in Place?If Nn, F.xplain
D Yes D No S Not ApplicableD Yes D No ^ Not ApplicableD Yes D No S Not ApplicableD Yes D No
Was Casing Cut Off Below Surface? D Yes D NoDid Sealing Material Rise to Surface? ^ Yes D NoDid Material Settle After 24 Hours? D Yes [X] NoIf Yes, Was Hole Retopped? D Yes D No
(5) Required Method of Placing Sealing MaterialW Conductor Pipe - Gravity LJ Conductor Pipe - PumpedCD Dump Bailer CD Other (Explain)
(6) Sealing Materials For monitoring wells andCD Neat Cement Grout monitoring well boreholes onlyCD Sand-Cement (Concrete) GroutCD Concrete CD Bentonite PelletsCD Clay-Sand Slurry CD Granular BentoniteCD Bentonite-Sand Slurry CD Bentonite-Cement GroutLXJ Chipped Bentonite
No. YaFrom (Ft.) To (Ft.) Sacks Se
or Volu
Surface 39.0 12 B
ids,alant Mix Ratio or Mud Weightme
ags
(8) Comments
(9) Name of Person or Firm Doing Sealing WorkBoart Longyear
Signature of gej^on Doiag \Work
Street or Route101 Alderson Street
Date Signed
Telephone Number
(715) 359-7090City, State, Zip Code
Schofield, WI 54476DNR/COUNTY
State of WisconsinDepartment of Natural Resources
Route To:D Solid Wastel~l Emergency Responsel~l Wastewater
D Haz. Wastel~| Underground TanksD Water Resourcesn Other
Soil Boring Log InformationForm 4400-122 7-91
Page 1 of 3Facility/Project Name License/Permit/Monitoring Number
National Presto Industries-Lagoon No. 1Boring NumberB-19A
Boring Drilled By (Firm name and name of crew chief) Date Dril l ing Started Date Dril l ing CompletedBoart Longyear (Mike Mueller)
DNR Facility Well No. WI Unique Well No.
Boring LocationState Planesw l / 4 o f S W 1/4 of Section 34
CountyChippewa
Sample
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Drilling Method
HSA
Common Well Name Final Static Water Level Surface Elevation Borehole Diameter
FeetMSL Feet MSL 7.0 InchesLocal Grid Location (If applicable)
N, E Lat ° ' " n N n E
T 28 N,R 9 W Long ° ' " Feet D S Feet D WDNR County Code9
Soil/Rock DescriptionAnd Geologic Origin For
Each Major Unit
Brown medium togravel
coarse sand with some
Same as above, few gravel
Same as above
C/3UC/5DSW
Civil Town/City/ or VillageEau Claire
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I hereby certify that the information on this form is true and correct to the best of my knowledge.Signature Firm Edcr Associates
8025 Excelsior Drive Madison, WI 53717Tel: (608)836-1500 Fax: (608)831-3337
This form is<a/uthm#e6/'by Chatffefs 144, 147 and 162, Wis. Stats. Completion of this report is mandatory. Penalties: Forfeit not less than $10 normore than $5,000 for each violation. Fined not less than $10 or more than $100 or imprisoned not less than 30 days, or both for each violation.Each day of continued violation is a separate offense, pursuant to ss 144.99 and 162.06, Wis. Stats.
State of WisconsinDepartment of Natural Resources
Soil Boring Log Information SupplementForm 4400-122A 7-91
Boring Number B-19A Use only as an attachment to Form 4400-122. Page 2 of 3Sample
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-29
-30
-31
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Soil/Rock DescriptionAnd Geologic Origin For
Each Major Unit
Same as above
Same as above
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State of WisconsinDepartment of Natural Resources
WELL/DRILLHOLE/BOREHOLE ABANDONMENTForm 3300-5W H_89
All abandonment work shall be performed in accordance with theAdmin. Code, whichever is applicable. Also, see instructions on
provisions of Chapters NR 111, NR 112 or 141, Wis.back.
GENERAL INFORMATIONWell/Drillhole/Borehole CountyLocation Eau Claire
D El /4of 1/4 of Sec. ;T. N; R l ~ ~ l w
(If Applicable)finv't I,ni Grid Number
Grid Locationft. n N n s.t ft. n E. n w.
Civil Town Name
Street Address of Well
City, VillageChippewa Falls
(2) FACILITY NAME PRESTOOriginal Well Owner (If Known)
Present Well OwnerPRESTO
Street or Route
City, State, Zip CodeChippewa Falls, WI
Facility Well No. and/or NameB-19A
Reason For AbandonmentTest Boring
Date of Abandonment9-17-96
(If Applicable) WI Unique Well No.
WELL/DRILLHOLE/BOREHOLE INFORMATION(3) Original Well/Drillhole/Borehole Construction Completed On
(Date)
LJ Monitoring Well Construction Report Available?D Water Well E3 Yes D No^ DrillholeD Borehole
Construction Type:E Drilled D Driven (Sandpoint) CH DugPI Other (-Specify^
Formation Type:K Unconsolidated Formation 1 1 Bedrock
Total Well Depth (ft) Casing Diameter fins }(From groundsurface)
Casing Depth (Ft )
Was Well Annular Space Grouted? D Yes D No D UnknownIf Yes, To What Depth'' Feet
(7)Sealing Material Used
Bentonite Chips
(4) Depth to Water (Feet) DryPump & Piping Removed?Liner(s Removed?Screen Removed?Casing Left in Place?If No, Fiplain
D Yes D No S Not ApplicableD Yes D No S Not ApplicableD Yes D No ^ Not ApplicableD Yes D No
Was Casing Cut Off Below Surface? D Yes D NoDid Sealing Material Rise to Surface? ^ Yes D NoDid Material Settle After 24 Hours? D Yes E3 NoIf Yes, Was Hole Retopped? D Yes D No
(5) Required Method of Placing Sealing MaterialS Conductor Pipe - Gravity 1 1 Conductor Pipe - PumpedD Dump Bailer CD Other (Explain)
(6) Sealing Materials For monitoring wells andLJ Neat Cement Grout monitoring well boreholes onlyLJ Sand-Cement (Concrete) GroutD Concrete CD Bentonite PelletsLJ Clay-Sand Slurry LJ Granular BentoniteEH Bentonite-Sand Slurry CD Bentonite-Cement GroutS Chipped Bentonite
No. YaFrom (Ft.) To (Ft.) Sacks Se
or Volu
Surface 36.0 1 1 B
rds,alant Mix Ratio or Mud Weightme
ags
(9) Name of Person or Firm Doing Sealing WorkBoart Longyear
Signature of Person Doine Work
Street or Route 14~101 Alderson Street
Date SignedI f\ *7 f~\lit j — ^x — ^vLO
Telephone Number(715) 359-7090
City, State. Zip CodeSchofield, WI 54416
'^^•^•^f^$m55
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DNR/COUNTY
State of WisconsinDepartment of Natural Resources
Route To:D Solid WasteD Emergency ResponseCH Wastewater
D Haz. WasteD Underground Tanksl~l Water ResourcesD Other
Soil Boring Log InformationForm 4400-122 7.91
Page 1 of 2Facility/Project Name License/Permit/Monitoring Number
National Presto Industries-Lagoon No. 1Boring NumberB-20
Boring Drilled By (Firm name and name of crew chief) Date Dril l ing Started Date Drill ing CompletedBoart Longyear (Mike Mueller)
DNR Facility Well No. WI Unique Well No.
Boring LocationStateSW
Planel / 4 o f S W 1/4 of Section 34
CountyChippewa
Sample
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-10
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09/17/96 09/17/96
Drilling Method
HSA
Common Well Name Final Static Water Level Surface Elevation Borehole DiameterFeet MSL Feet MSL 7.0 Inches
Local Grid Location (If applicable)N, ET 28 N . R 9 W I
T nr vi i iiLat n N n E_x>ng ° ' " Feet D S Feet D W
DNR County Code9
Soil/Rock DescriptionAnd Geologic Origin For
Each Major Unit
Brown medium togravel
Same as above
Same as above
coarse sand with some
C/2U
DSW
Civil Town/City/ or VillageEau Claire
0
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I hereby certify that the information on this form is true and correct to the best of my knowledge.Signature Firm Eder Associates
8025 Excelsior Drive Madison, WI 53717Tel: (608)836-1500 Fax: (608)831-3337
This form iyau^oVieey by Chapters 144, 147 and 162, Wis. Stats. Completion of this report is mandatory Penalties: Forfeit not less than $10 normore than $5,000 for each violation. Fined not less than $10 or more than $100 or imprisoned not less than 30 days, or both for each violation.Each day of continued violation is a separate offense, pursuant to ss 144.99 and 162.06, Wis. Stats.
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Blow Counts
Depth In Feet
Soil/Rock Description
And G
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ajor Unit
u s e sGraphicLogWellDiagram
PID/FID
StandardPenetrationMoistureContentLiquidLimitPlasticLimit
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RQD/Comments
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State of WisconsinDepartment of Natural Resources
WELL/DRILLHOLE/BOREHOLE ABANDONMENTForm3300-5W 11-89
All abandonment work shall be performed in accordance with the provisions of Chapters NR i l l , NR 112 or 141, Wis.Admin. Code, whichever is applicable. Also, see instructions on back.
GENERAL INFORMATIONWell/Drillhole/BoreholeLocation
1/4 of 1/4 of Sec(If Applicable)
flOV't \M
Grid Locationft. n N n s ,
County
Eau ClaireD E
;T. N:R CD W
find Number
ft n E. n wCivil Town Name
Street Address of Well
City, Village
Chippewa Falls
(2) FACILITY NAME PRESTOOriginal Well Owner (It Known)
Present Well Owner
PRESTOStreet or Route
City, State, Zip CodeChippewa Falls, WI
Facility Well No. and/or Name
B-20(If Applicable) WI Unique Well No.
Reason For AbandonmentTest Boring
Date of Abandonment9-17-96
WELL/DRILLHOLE/BOREHOLE INFORMATION(3) Original Well/Drillhole/Borehole Construction Completed On
fDatel
CD Monitoring WellD Water WellS DrillholeD Borehole
Construction Type:S Drilled D Driven["I Other (Specify^
Formation Type:£3 Unconsolidated Formation
Construction Report Available?S Yes D No
(Sandpoint) CD Dug
D Bedrock
Total Well Depth (ft) Casing Diameter fins >(From groundsurface)
Casing Depth (Ft 1
Was Well Annular Space Grouted?If Yes, To What Depth?
D Yes D No D UnknownFeet
(7)Sealing Material Used
Bentonite Chips
(4) Depth to Water (Feet) DryPump & Piping Removed?Liner(s) Removed?Screen Removed?Casing Left in Place?If No, Piplain
D Yes D No S Not ApplicableD Yes D No S Not ApplicableCD Yes D No K Not ApplicableD Yes D No
Was Casing Cut Off Below Surface? D Yes D NoDid Sealing Material Rise to Surface? 13 Yes CD NoDid Material Settle After 24 Hours? D Yes S NoIf Yes, Was Hole Retopped? D Yes D No
(5) Required Method of Placing Sealing MaterialS Condv-'-- IV-~ °~jviry CD Conductor Pipe - PumpedCD Dump Bailer D Other (Explain)
(6) Sealing Materials For monitoring wells andCD Neat Cement Grout monitoring well boreholes onlyCD Sand-Cement (Concrete) GroutCD Concrete CD Bentonite PelletsCD Clay-Sand Slurry CD Granular BentoniteCD Bentonite-Sand Slurry CD Bentonite-Cement GroutIXJ Chipped Bentonite
No. YaFrom (Ft.) To (Ft.) Sacks Se
or Voli
Surface 31.0 11 B
rds,alant Mix Ratio or Mud Weightime
ags
(9) Name of Person or Firm Doing Sealing WorkBoart Longyear
Signature of Person Doing Work
/<• —— -T^Lst^i-^^Street or koutc *101 Alderson Street
Date Signed
/0-S-quTelephone Number(715) 359-7090
City, State, Zip CodeSchofield, WI 34476
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APPENDIX B
APPLICABLE OR RELEVANT AND APPROPRIATE REOUIREMENTS
LLV59JO HIT
The following listing of ARARs has been extracted from the May 1996 ROD for the NPI site
remedy. A number of these ARARs would apply to the Lagoon No. 1 response action.
LLV59MWT
B.
The selected remedy will meet all ARARs under federal, and more stringem state environmentallaws. A IistofARARsforthc She is contained in Tables 2 and 3, The primary ARARs that willbe achieved by the selected remedy are:
1. Chemical gpriffr
Chemical-specific ARARs include those laws nod requirements that regulate the release ofcontaminants to the environment These include:
cu [42 U-S'C § 7401 rt ""I* ™»»l» Environmental Protection Law,Subchapter Hi-Air PoOntion [Wii. Stat 144JO-144.426J
40CFR 50; Wis. .Admin. Code NR 404. 445- Air Pollution Control Regulation*. These regulationsestablish standards for emission of pollutants into the ambient air. Since the selected remedyinvolves excavation, construction and SVE activities which inayrdt^rontainiriaiitsorpaiticulatcsinto the air.emis3ion requirements promulgated under this act are relevant and appropriate. Theneed for treatment of air emissions p-duced by these processes would be determined based on^**vc | requirements of Wis. Admin. Code NR 445. If emissions are expected to exceed thosestandards, the remedy wfll be designed to reduce such emissions to acceptable levels or provide fortreatment to satisfy these Wisconsin standards.
Safe Drinking Water Act [40 U.S.C. § 300 et seq.J
40 CFR141, Wis. Admm. Code NR 109 - MCU. MCLs establish drinking-water standards forpotential and actual drinking water sources. MCLs have been exceeded at the Site in the aquiferaffected by Plume 1*2 which is presently being used as a drmkmg vwtter source by the City of EauUame. A two-column air-stripper currently treats the water in Plume 1 -2 before hs distribution tothe municipal water supply. Water treated by the air strippers meets all MCLs and non-zero
Level Goals fMCLGs"). MCLs have also been exceeded in Plumes 3 andgCr SCIVC •* a drinkinB watcr suPPly- MCLs have been attained, but not exceeded,
in Flume 5. which also no longer serves as a drinking water supply. The selected lemedy achievescompliance with MCLs and non-zero MCLGs.
Wis. Admin. Code NR140- Ground Water Quality Standards. These standards provide for groundwater quality standards including PALs, Wisconsin ESs, and Wisconsin Alternative ConcentrationLimits ( WACLs"). The selected remedy, building on the previous OU.% is intended to achieve
compliance with PALs at all monitoring points. To the extent ILS. EPA 's 5-year reviews indicatethat h is not technically or economically feasible to achieve'PALs, NR140.28 provides substantivestandards for granting exemptions from the requirement to achieve PALs. Such exemption levelsmay not be higher than the Wisconsin ESs. U.S. EPA also has a procedure for granting a technicalimpracticability waiver under CERCLA.
Wisconsin Environmental Protection Law, Sabchapter Il-Water and Sewage [Wis. Stat§ 144.02-27]
Wis. Admin. Code NR 102 and 105 - Surface water quality standards. NR 102 creates anantidegradation policy for all waters of the state and prohibits toxic substances in surface waters atconcentrations which adversely affect public health or welfare, present or prospective water supplyuses, or protection of animal life. Surface water samples collected from Lake Hallic during the RIshowed that contaminant concentrations were well below Wisconsin surface water quality standards.
Toxic Substances Control Act (15 U.S.C § 2601 et seq.)
40 CFR 761; Wis. Admin. Code NR 157 - Management of PCBs and Products Containing PCBs.These provisions are applicable to the storage, collection, transportation, processing and finaldisposal of PCBs and products containing PCBs.
2. Action Specific
Wis. Admin. Code NR 141 - Ground-Water Monitoring We'd Requirements. These requirementsestablish minimum acceptable standards for the design, installation, construction, abandonment anddocumentation of ground-water monitoring wells, and are applicable to the existing monitoring wellsand any to be installed as part of the long-term monitoring piugiuiii.
Wis. Admin. Code NR 718 - Management of solid wastes excavated during response actions. Theserequirements are applicable for the storage, transportation, treatment and disposal of contaminatedsoil and certain other solid wastes excavated during response actions.
Wis. Admin. Code NR 720 - Soil Cleanup Standards. These soil standards were developed based onthe ground-water standards (PALs) of Chapter NR 140 for the ground-water exposure pathway.These soil standards were designed to assure that ground-water standards will not be exceeded dueto leaching of residual contamination from the soil to the ground water. These requirements applyto soils remaining at Ditch No. 3 and the East Disposal Site after excavation and consolidation at theMelby Road Disposal Site.
Resource Conservation and Recovery Act ("RCRA"), as amended {42 U.S.C. § 6901 et seq.J;Wisconsin Environmental Protection Law, Hazardous Waste Management Act (Wis. Stat.§ 144.60-74]
Most federal RCRA requirements are administered under the State of Wisconsin's equivalentregulations. U.S. EPA has determined that the waste forge compound contains the spent solventTCA which is a listed hazardous waste pursuant to NR 605.09 of the Wisconsin Administrative Code(Wisconsin's equivalent to the federal table of hazardous wastes from non-specific sources, 40C.F.R- § 261.31). Excess forge compound generated during NITs production processes was mixedand co-disposed of with spent TCA, forming a combined waste stream which must be treated as alisted hazardous waste. RCRA hazardous waste treatment and disposal regulations arc thereforrapplicable. The following requirements are also applicable or relevant and appropriate:
Wis. Admin. Code NR 60S; 40 CFR 261 - Identification of Hazardous Wastes. Providesrequirements for determining when a waste is hazardous. The substantive requirements of theseregulations will apply to any on-site TCLP testing of treatment residuals and waste excavated at theSite which may be disposed of off-site.
Wis. Admin. Code NR 615; 40 CFR 262 - Standards Applicable to Generators of Hazardous Waste.These standards provide requirements for the shipment of wastes to treatment, storage or disposalfacilities. These requirements apply to on-site preparations for off.jate shipment of dry well soilsand other wastes.
Wis. Admin. Code NR 620; Department ofTransportation Hazardous Materials Transportation Act[49 U.S.C § 1801]; 40 CFR 263 - These standards arc applicable to transporters ofhazardous waste.They require record keeping, reporting and manifesting of waste shipments. These requirementsare relevant and appropriate to on-site preparations for off-site shipment of dry well soils and otherwastes.
Wis. Admin. Code NR 630.10-17; 40CFR264. Subpart B - General Facility Requirements. Theserequirements establish substantive requirements for security, inspection, personnel training, andmaterials handling which are relevant and appropriate to on-site activities involving excavations andhandling ofhazardous soils and materials.
Wis. Admin. Code NR 630.21-22; 40 CFR 264. Subpart D - Contingency Plan and EmergencyProcedures. These procedures establish substantive requirements for emergency planning whichare relevant and appropriate for on-site activities involving excavation and handling of hazardoussubstances.
Wis. Admin, Code NR 675; 40 CFR 268 - Land Disposal Restrictions ("LDRs"). These regulationsgovern the storage and land disposal of hazardous waste. Consolidation of waste materials willoccur within the area of contamination at the NPI Site. Therefore, the requirements of theseregulations will not be triggered for on-sitc soil consolidation. LDR requirements will be applicable.
however, to any off-site treatment of the wastes excavated from Dry WeUs 2 and 5 or hotspot wastesexcavated from Melby Road that are RCRA hazardous waste.
3. Location -Specific
Location-specific ARARs are those icquiiements that relate to the geographical location of a site.No location-specific ARARs have been identified for this action.
NATIONAL PRESTO INDUSTRIES, INC. SITEEAU CLAIRE, WISCONSIN
TABLE 2
APPLICABLE OR RELEVANT AND APPROPRIATEFEDERAL REGULATIONS
Slandaid. Requirement. Crilerion or 1 .imitation Cilallon Description
Stlt Orlnklnt Wate r Act 41 U.S.C. 5 JOOg
Ntlional Primary Diinklnj Water Slandaidt
Nillonal Secondary Drinking Water Slanduds
Minimum Conlamlnani Level Go ill
40CFRI4 I
40CFR 14)
Public Law 99-3)9
EiUbllshcs health-based standards (maximum conlamlnani levels) Tor public water supply syslcnu.
Establishes welfare-based standards (secondary MCLs) for public water supply syslcnu.
Esublilhci drinking walci quality |oall al levels that are nol known or anilclpalcd lo produce adverse health cfTcclj, with anadequate mwfln of safety. Only non-zero MCLOl are ARAJU.
Clean Air Ael 41 U.S.C. | 7401-7(41
tUtlond Primary and Scconduy Ambient AirQuality Slanduds
National Emission Slandaids fur Hazardous AirPollutants
40CFR50
40CFR6I
EiUbllshcs ambient air quality standards (Includini; lead and particulars) lo control polnl source air emissions and prolecl publichealth and welfare.
Establishes emission standard! for designated hazardous air pollutants.
Solid Wult Dhpoul Act 41 U.S.C. f, 6901-69S7
Idcnlincalion and Listing of I lazaidous Waste
Slanduds Appliciblc lo Gtncralors ofHazardous Waste
Standards Applicable lo Transporters ofllaraidous SVasle
40CFR261
40CFRJ62
49CFR26)
Identifies solid wules subject lo regulation u huardous wailcs.
Establishes sUndards for |cneialon ofRCRA wastes.
Establishes ilandardj applicable lo transporter! of RCRA wulcs.
Table 2 Cont inued . . .
Sluidud. Requirement, Cilleiion 01 Limitation
Slindudi for Owners uid Operilorj oflluudoui Wisle TSU Ftcllilici
1 ind Diipoiil RciUiclloiu
CiUllon
40CFR 364
40CFR261
Description
EiUbllshcl minimum lUndudi for muii(ln( f»cllillcs thil Ircil, iiorc or dlipotc of htuudoiu wrulc
Idcnilfici huudoui wrutc prohibited from land dlipostJ and iltutllonj where luid dispoul It icccpliblc
Iliurdoui Mtlcrlili Triniportitloo Ac) 41 U.S.C. | 1101-IIIJ
llxudoui Miterltlt
I o i l c Sutul infc i (
Irtntportillon Rcgulilioru 49CFR 107.171-177 Eiltbllihct lUndudj for btniporUllon of huudou) wuics
o n l r o l A f l 1 S U.S.C. | 1601-
1(29
PC'11 RcquircmcnU 4 0 C I R 7 6 I . l:>l»bliihcl PCD wulc ilori|c uid dllpoill requlrcfncnl)
I S.C. = United States Code:i:l(. = Code of Federal Regulations
NATIONAL PRESTO INDUSTRIES, INC. SITEEAU CLAIRE, WISCONSIN
TABLE 3
APPLICABLE OR RELEVANT AND APPROPRIATESTATE REGULATIONS
Sltndud, Kcquircnicnl, Ciilciion 01 1 imililion
Wisconsin Ground Water Quilily Slinduds
Ground Wilti Monitoring Well Requirement!
Wild Quility Slandudi fur Wiiconiin SmficcWate rs
Surface Wilcr Quilily Crilciii fur foxicSubstances
lli.fifdoui Wulc Management
——————————————————————————————————
Wisconsin Solid Wislc Mtntgcrncnl Regulations
Investigation ind Remediation of UnvirontnenltlContamination
Mirugcincnl of PCUs tnd Product! ContainingPCIll
Wisconsin Air Pollution ConUol Regulations» Wisconsin Drinking Wilci Rules
Cililion
WAC. Ch MR 140
WAC. Ch NR 141
WAC. Ch. NR 102
WAC. Ch NR 105
WAC, Chi. NR600615
WAC. Chs. NR 500520
WAC. Clu. NR Ti l-776
WAC. Ch NR 157
WAC. Chs. NR 404.445
WAC. Ch NR809
Dcicrlpllon
Esltbliihci subsltntc specific ground wilci qullily sUnduds. groundwtlcr stmpllng tnd tntlysis procedures, tnd itngcs oficspontct Ihtl miy be required If t groundwilci qutlily iltndud is exceeded
Esltblishci ground-wilci monitoring well sUnduds.
nsltblishci suffice wilci qutlily sUnduds Ihtl piotccl Die public Interest; deslgntlei Ihc use ctlcgoilcs of (lie suiftcc wilciswilcr quality cille rii Ihtl support these uses.
and (he
Uslibllshcs in-slietm surfice wilci ilandudi for protection of tquallc life.
lisltbllshcs hauidoui wulc Idenllflcillon crllerli, minimum iltnduds fat harudout wulc management and handling, andhua/doui wule facility closure standards thai protect health and Ihc cnvlionmcnt.
Esliblishes procedures for handling solid wulc; licensing and operating solid waste management facilities; solid wutc disposilfacility performance standard] and design, monlloring, icportlng and closure requirements; and land spreading requirements
Eslabllshcs the procedures and standards for cleaning up contaminated sites
Establishes procedures for handling and disposing of PCDs tnd product! containing PCRs, and establishes methods for sampling,preparing samples and analyzing such materials for PCUs.
Establishes primary and secondary ambient air quality standards and pollutant-specific emission linuiiiions lo maintain iccepubleair quality and protect public health and Ihc environment.
Eslabllshcs mulmurn contaminants levels allowed In drinking walcr.
APPENDIX C
IRA GRQUNDWATER REMEDIATION SYSTEM TIME FRAME ESTIMATES
LLV59M WT
ESTIMATED IRA REMEDIATION SYSTEM TIME FRAME
The operating time for the IRA system at the southwestern portion of the NPI site (downgradient of
Lagoon No. 1) was estimated using a variation of Darcy's Law. This estimate assumes that the
source of VOCs has been eliminated by the SVE, composting or off-site landfilling alternatives
evaluated for the lagoon vadose zone soil in this EE/CA.
Darcy's Law Q = KIA
Q = Discharge (fWday)K = Hydraulic conductivity (ft/day)
A = Cross-sectional area of the aquifer (ft2)
I = Hydraulic gradient (ft/ft)
The following modified version of Darcy's Law enables time to be calculated.
v = ££
V = Velocity (ft/day)
T = Time (day)
D = Distance (ft)
LLV59M RJ»T *"" '
K = Hydraulic conductivity (ft/day)
I = Hydraulic gradient (ft/ft)
u = Porosity (%)
The operating time for the IRA system was calculated using conservative parameters. The selected
particle pathway from the eastern side of Lagoon No. 1 to IRA Extraction Well 4 is shown on Figure
1, and represents the longest pathway to the extraction well. According to Eder's Groundwater
Modeling Study Report (January 1994), the hydraulic conductivity through the site varies from 140
to 270 feet per day. For the purpose of this evaluation, 140 feet per day was used. The hydraulic
gradient varies from the eastern side of Lagoon No.l to Extraction Well 4 due to the hydraulic
influence of the extraction well. Thus, the operating time of the IRA system was calculated across
two distances using the appropriate hydraulic gradients calculated from Figure 1.
Parameters for the zone of no influence from extraction wells:
DAB = 575 feet
K =140 feet/dayI = 0.006
u =0.3
T = 205 days
Parameters for the zone of influence from extraction wells:
DBC = 450 feet
K =140 feet/day
I =0.01
u =0.3
T =96 days
U.V59JORJT C-2
The total time is 301 days. This period is multiplied by a retardation factor of six (consistent with
the assumptions in the Eder's Groundwater Modeling Study Report (January 1994)), yielding 1806
days or 4.9 years.
This evaluation indicates that the IRA system at the southwestern portion of the NPI site would
operate for approximately five years under the alternatives (SVE, composting, off-site landfilling)
that would remove the low level source of VOCs remaining at the Lagoon No. 1 area. The IRA
system would be expected to operated at least twice as long (10 years) if the source remains in place
under the no further action alternative. These time frames are used to evaluate and compare the
Lagoon No. 1 vadose zone alternatives in this EE/CA.
LLV59IO RPT C-3