YOUNGSTROM LOG HOMES
FINAL REMOVAL ACTION REPORT
TDD: 96-10-0006
Contract No: 68-W6-0008
June 23, 1997
REGION X
START
SUPERFUND TECHNICAL ASSESSMENT & RESPONSE TEAM
Prepared for:
W ^ ^ J
SEZ
EPA
Office of Environmental Cleanup
Region X
CARL KITZ
ON-SCENE COORDINATOR
Prepared by:
¦¦ ecology and environment, inc.
W Seattle, Washington (206) 624-9537
International Specialists in the Environment
JERYL KOLB
PROJECT MANAGER
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June 23, 1997
Mr. Gary Sink
START X Project Officer
U.S. Environmental Protection Agency
1200 Sixth Avenue, Mail Stop ECL-116
Seattle, WA 98101
RE: Contract 68-W6-0008
TDD: 96-10-0006
Dear Gary:
Please find enclosed the final removal report for the Youngstrom Log Homes removal action in
Blackfoot, Idaho. Removal activities occurred from November 7-21, 1996, and primarily involved the
sampling, hazard characterization, and off-site disposal of approximately 1,000 drums and containers
consisting of eleven different wastestreams. The site is located at an abandoned log home construction
facility situated on the Fort Hall Indian Reservation, and it is believed the containers were brought to the
site for disposal by third parties.
If you have questions or comments, please do not hesitate to contact me at (206) 624-9537.
Sincerely,
Noah Myers
START Project Leader
JTK/jw
Enclosure
cc: Carl Kitz, On-Scene Coordinator, U.S. EPA, Seattle, WA (Mail Stop ECL-116)
William Carberry, START Program Manager, E & E, Inc., Seattle, WA
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TABLE OF CONTENTS
Section Page
1.0 INTRODUCTION 1
2.0 SITE BACKGROUND 1
2.1 Site History 1
2.2 Environmental Setting 1
2.3 Previous Investigations 3
3.0 REMOVAL ACTIVITIES 3
3.1 Objectives and Strategy 3
3.2 Chronology of Events 5
3.3 Drums and Containers 7
3.4 Investigation of Soil Contamination 8
3.5 Other Wastes 10
3.6 Final Waste Disposition 12
4.0 COST SUMMARY 12
5.0 CONCLUSIONS 12
REFERENCES
APPENDICES
Appendix A U.S. EPA Removal Assessment Report
Appendix B Action Memorandum
Appendix C Site Photographs
Appendix D Pollution Reports
Appendix E Container Inventory
Appendix F Hazard Categorization Data
Appendix G Immunoassay Test Kit Information
Appendix H Uniform Waste Manifests
Appendix I Idaho State Journal Newspaper Article
LIST OF FIGURES
Figure Page
1 Site Location 2
2 Site Features 4
3 Test Pit Locations 9
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FINAL REMOVAL ACTION REPORT
YOUNGSTROM LOG HOMES
BLACKFOOT, IDAHO
TDD: 96-10-0006
1.0 INTRODUCTION
The U.S. Environmental Protection Agency (EPA) Region 10 Environmental Clean-up Office
tasked the Ecology and Environment, Inc. Region 10 Superfund Technical Assessment and Response Team
(START) to assist in time-critical removal activities at the Youngstrom Log Homes
(Youngstrom) site located in Blackfoot, Idaho.
The site is located on property owned by the Shoshone-Bannock Tribe, who requested EPA
assistance for removal activities after they determined they could not meet the financial demands required
for a clean-up.
2.0 SITE BACKGROUND
2.1 Site History
The Youngstrom site is a former sawmill and fabricated log home construction facility located
entirely within the boundaries of the Fort Hall Indian Reservation, and the jurisdiction of the Shoshone-
Bannock Tribe. The property was leased by Mr. Lewis Youngstrom from the tribe starting on an unknown
date. In addition to the log home business, Mr. Youngstrom apparently used the property to store solid and
hazardous waste which he accepted from third parties, and conducted a small amount of gravel quarrying.
No wood treatment operations have been alleged. The tribe revoked Mr. Youngstrom's lease in 1987, and
he promptly abandoned the property. The site remains inactive and has increasingly become an attraction to
vandals and trespassers (E & E 1992).
2.2 Environmental Setting
The site is situated approximately three miles south of the town of Blackfoot, Idaho, in Bingham
County, on the west side of State Highway 91 and approximately 0.5 miles south of Interstate 15 (Figure 1).
The surrounding area is primarily rural and agricultural, and a few scattered homes are located within
approximately one hundred yards of the site. A commerical cigarette business is also located immediately
adjacent to the site property along Highway 91.
An agricultural irrigation canal forms the northern, and a portion of the western, site boundaries;
Highway 91 borders the site on the east; and the remainder of the site is surrounded by agricultural
property. While the approximately 10-acre site is fenced, this consists of a split log fence along the
highway and a two-strand barbed wire fence around the remaining perimeter, and thus access can be gained
by persons on foot. The northern half of the site consists of approximately 20 buildings of various sizes
that were used for different wood-product activities. Most of these buildings are deteriorating and open to
the elements, and all but two or three are constructed of wood. The remainder are fabricated from sheet
metal.
The southern half of the site is largely open and vegetated with grasses and weeds. There are
several piles of wood debris and soil, as well as stockpiles of containers varying in capacity from 55-gallons
to 1-quart. There are also smaller piles of metal junk, empty vats and tanks, and abandoned
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ecology and environment, inc.
International Specialists in the Environment
Seattle, Washington
YOUNGSTROM LOG HOMES
Blackfoot, Idaho
Figure 1
SITE LOCATION MAP
No Scale Used
Drawn By
MRE
Date
2-4-97
Job No.
AJ0601RATO
Dwg.No.
AJ0601F1
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vehicles, as well as several trenches or pits where gravel was apparently excavated and removed. Some of
these have been partially re-filled with sawdust (Figure 2).
2.3 Previous Investigations
The EPA conducted an assessment of the site in 1992 in order to determine if removal activities
were warranted. This assessment was precipitated by repeated requests for assistance from the tribe and
observations of the site made by EPA Resource Conservation and Recovery Act (RCRA) inspectors during
a routine compliance visit in 1991 (Appendix A)(E & E 1992).
The site assessment documented the presence of approximately 500 containers, some of which the
contents appeared to have spilled or leaked onto the ground. Samples were collected from 16 of the
containers and analyzed in the field for hazardous characteristics. Based on those results, seven of the
samples were sent to a commercial laboratory for further analysis, which revealed a broad range of volatile
organic compounds (VOCs), semivolatile organic compounds (semivolatiles), pesticides, and heavy metals.
In addition, nine soil and two groundwater samples were collected. Elevated concentrations of semivolatiles
and heavy metals were detected in the soil samples, which were collected primarily from biased locations
around the container stockpiles. The two groundwater samples, which were collected from the on-site water
well, did not contain any concentrations above primary or secondary Maximum Contaminant Levels (E & E
1992).
Based on these findings, the EPA recommended a removal action be conducted due to the threats
represented by the containers and soil contamination, the accessible, remote nature of the site, and the
continuing problem with trespassing. As part of the previous RCRA inspection, the EPA had attempted to
contact Mr. Youngstrom, however he had died since abandoning the site. His son possessed very little
knowledge of site operations, and repeated attempts by the tribe to fund a removal through Mr.
Youngstrom's estate failed due to lack of funds. At this point, the tribe again requested assistance from the
EPA (E & E 1992).
3.0 REMOVAL ACTIVITIES
3.1 Objectives and Strategy
Based on information obtained through the EPA site assessment and tribal representatives, the
objectives of the removal action were to fully characterize all on-site containers and other potential areas of
concern, and then remove any hazardous materials or waste off site for disposal. In addition to the
containers, this would involve investigating piles of soil and debris, areas of gravel excavation, and site
buildings for extent of contamination (E & E 1996). This would reduce the threat these features repre-
sented to the surrounding public and the environment. In order to reduce the threat of on-going trespassing
and vandalism, including the possibility of further waste disposal by area residents, the entire perimeter of
the site would be secured with a chain-link fence (E & E 1996).
A strategy was devised for implementing these objectives that involved moving all the containers to
a central location where they could be staged, opened, and sampled, and the samples analyzed. This was
necessary because the containers were located in several stockpiles that would have made sampling
activities logistically difficult and unsafe. This central staging area needed to be large enough to
accomodate all the containers, and yet secure enough to provide shelter from weather conditions. Because
the site had been inactive for nearly a decade, it was realized that the location
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chosen for this staging area would require stabilization and clean-up prior to being used (E & E 1996).
This was a concern partially because of reported cases of Hanta virus infections on parts of the reservation.
Infection can occur through contact with dried rodent feces or urine, and can be fatal.
Additional areas of concern, including possible soil contamination, would be investigated using a
backhoe and excavation techniques. Interest would lie primarily in areas where debris, junk, or stained soil
was encountered. Soil samples would be collected and analyzed on site. The objective of these activities
would partly be to help determine if wood treating activities occurred while the site was active.
3.2 Chronology of Events
April, 1992: The EPA conducted an assessment of the site in order to establish if threats to the public
and/orenvironmentexisted,andwhetherremovalactivitieswerewarranted. Thisinvolvedinventoryingthecontainers,
collecting samples from 16 of them, collecting soil and groundwater samples, and analyzing the samples on site
for hazardous characteristics. Based on the data and observations collected, the EPA determined that a removal
was justified to reduce the threat posed by the containers.
August, 1996: The Shoshone-Bannock Tribe, deciding they could not fund removal activities, requested
assistance from the EPA. A short visit to the site was performed by the EPA and START, and the activities
and conclusions of the EPA site assessment were reviewed.
October 25,1996: After the Action Memorandum (Appendix B) was completed and signed, and removal
activities authorized, the EPA, START, and the Emergency Response Clean-up Services (ERCS) contractor
met to discuss removal logistics and objectives.
October 29,1996: The START and ERCS conducted a short visit to the site in order to more conclusively
determine the number and size of containers, decide on the location of a central staging area, and meet with tribal
representatives to apprise them of removal objectives. Photos documenting site conditions are provided in Appendix
C.
November 7,1996: The EPA, START, and ERCS mobilized to the site. The parking bays and lean-to
attached to the north end of the office building were selected as the staging area, and ERCS began sweeping
and cleaning. Due to the threat of Hanta virus infection, cleaning was conducted with respiratory protection,
and the entire area was disinfected using a bleach solution. The ERCS also prepared locations adjacent to the
office building for mobilization of the office trailers, and heavy equipment was used to construct roads leading
to the container stockpiles. Once the staging areas were prepared, ERCS began transporting containers from
various stockpiles to the staging areas, starting with the parking bays. The START began setting up the hazard
categorization and sampling equipment, and initiated numbering, inventorying, and opening of the staged containers.
Pollution reports completed by the EPA, which documented removal activities, are provided in Appendix D.
November 8,1997: After the containers were staged, inventoried, and opened, the contents were sampled
and hazard categorized. Staging of the containers continued, with both the parking bays and lean-to completely
filled. Office trailers were mobilized to the site, and rental office equipment was delivered.
November 10,1997: The ERCS finished staging all the containers. In addition to the larger stockpiles,
there were individual containers scattered throughout the site. Some of these were in such poor condition they
required overpacking prior to being moved to the staging area. Due to overflow at the first staging area, a second
staging area was constructed west of the parking bays adjacent to a sheet metal building. The START continued
numbering, opening, inventorying, and sampling the containers, as well as analyzing the samples. Many of the
5-gallon containers consisted of pigmented sand that was non-hazardous and was probably used to color milled
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lumber. Due to the large number of containers with similar contents, the number of samples were reduced accordingly.
Based on the analytical data, ERCS began to consolidate and re-stage containers according to designated
wastestreams.
November 12,1996: Opening and inventorying the containers was completed. Based on the findings
from the inventory, it was determined the contents of the containers remaining to be sampled were similar enough
to allow abbreviated hazard analysis. In addition, because these remaining containers were so small, sample
collection was eliminated and analysis was conducted from aliquots obtained directly from the containers. As
a result of these actions, all sampling and analysis was also completed. The ERCS continued to re-stage containers
according to wastestream. All but one START member demobilized from the site with all unnecessary equipment
and supplies.
November 13,1996: At the direction of the OSC, the ERCS excavated test pits at six locations in a
search for possible soil contamination or buried waste. The START documented these activities and collected
a soil sample at each location. No indication of buried waste, soil staining, or contamination was found, and
the test pits were backfilled. The ERCS continued to re-stage containers according to wastestream and to arrange
for off-site disposal. This included collecting samples for analysis of VOCs and metals using Toxic Characteristic
Leaching Procedure (TCLP) methodology, as well as bulking smaller containers together into overpacks to facilitate
transportation off site.
November 14,1996: While the ERCS continued to re-stage and bulk containers, the START collected
an additional seven soil samples from selected locations around the site. These included spots where, during
a survey conducted earlier in the week, a metal detector had indicated buried metal, and background locations.
These samples, along with the ones collected the previous day, were analyzed for pentachlorophenol by START
using immunoassay test kits. The concentrations in all 14 samples were below detection limits. The START
also inventoried all electrical, monitoring, and other types of debris scattered around the site. This included
documenting manufacturers, model types, and serial numbers.
November 15,1996: ERCS finished bulking all wastestreams except those that would later be placed
directly into a roll-off box, as well as those that still required VOC and TCLP data.
November 18,1996: The parking bay area was used to re-stage overpacks prior to being labeled and
transported off site. This involved cleaning the area which had previously been used to stage and sample containers,
and then transporting each overpack from the secondary staging area, where a majority of the bulking occurred.
Empty drums discovered on site were crushed and stockpiled adjacent to the secondary staging area.
November 19,1996: A roll-off box for non-hazardous solid waste was delivered to the site and the crushed
drums and other wastes were placed into it. The box was completely filled and transported off site. The ERCS
also finished bulking the remaining wastestreams.
November 20,1996: Two roll-off boxes, one for non-hazardous solid waste and the other for hazardous
waste, were delivered to the site. The wastestream consisting of the pigmented sand was placed into the non-hazardous
box, while various types of investigation-derived waste such as visqueen, samples, and personal protective equipment
were placed into the hazardous box. Both boxes were then properly placarded, the manifests signed, and the
boxes transported off site. The START and ERCS began labeling the overpacks according to wastestream.
November 21,1996: A tractor trailer truck arrived at the site and ERCS began to load the overpacks
onto it according to wastestream. The START finished labeling the remainder of the overpacks prior to being
loaded, as well as documenting activities. All remaining wastestreams were loaded onto the truck and secured,
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and the truck was properly placarded. Once the manifests were completed and signed, the truck departed the
site. The OSC, START, and ERCS began to demobilize equipment and supplies.
November 22,1996: The office trailers and remaining heavy equipment were demobilized and the OSC,
START, and ERCS departed the site.
3.3 Drums and Containers
Removal activities addressing the drums and other containers began shortly upon mobilization to the
site. The ERCS began constructing staging areas for the containers in the parking bays and lean-to adjacent
to the office building. This location was chosen because it was close to the property entrance, had a
concrete floor, and was relatively sheltered from the weather. Regardless, prior to staging containers and
assembling work areas, the area still required cleaning and sweeping because of the possibility of Hanta
virus contact.
The ERCS also began using a bulldozer to build roads leading to the container stockpiles. This
process consisted of simply scraping and leveling the top layer of soil and vegetation in order to make
access and transport easier. The same thing was done to the area in front of the property entrance and
around the office building.
Once the parking bays and lean-to were sufficiently cleaned, visqueen was laid down and the
START began unloading equipment and building a work station for hazard categorization (hazcatting)
activities. This station was at the south end of the parking bays, and visqueen was spread through the
remainder of the area. The ERCS began loading 5-gallon containers from one of the stockpiles onto a pick-
up truck and transporting them to the parking bays. There they were unloaded and re-staged onto the
visqueen by hand. Once the parking bay was filled, visqueen was spread onto the ground under the lean-to,
and 5-gallon containers were staged there.
The START began numbering the containers as they were staged, and an inventory was started that
recorded the container number, size, integrity, and any markings or labeling that could be found (Appendix
E). Once a sufficient number of containers had been staged, the START began to open them in Level C
protection. Most of these 5-gallon containers had lids with metal tabs and, as they were opened, the volume
inside each container was recorded.
When they re-staged the containers, the ERCS concentrated on one stockpile at a time, and
containers of various sizes were segregated into certain locations within the staging area. As the lean-to
filled with 5-gallon containers, additional 1-gallon and smaller containers were staged immediately adjacent
to the east, while 55-gallon containers were staged immediately adjacent on the west side of the lean-to.
Once this area had been filled, a second staging area was constructed to the west of the office building in
front of the metal pole barn. This again involved bulldozing and leveling the area, and spreading visqueen
on the ground.
The START hazcatted samples after they were collected, and used this data to place containers into
a wastestream (Appendix F). The ERCS then began to re-stage containers according to the wastestreams.
This was done primarily at the second staging area, but several pallets of 1-gallon containers with paint
waste were also segregated. As more sampling and hazcatting was conducted, more data was obtained and
it became easier to determine which wastestream a container belonged in. This eventually resulted in
reduced sampling because, in some cases, the wastestream could be determined simply by looking at the
contents.
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While the containers were segregated into wastestreams, the ERCS began to bulk the contents into
overpacks. In some cases this meant placing several 5-gallon containers into 55-gallon or 85-gallon
overpacks, while for other wastestreams, the contents of the original container were emptied into the
overpack and the container was crushed and discarded.
Once all the containers had been sampled or checked, and the samples hazcatted, the ERCS
completed bulking and re-staging containers until they were all overpacked and ready for off-site disposal.
3.4 Investigation of Soil Contamination
A backhoe was used to excavate six test pits in order to investigate the possibility of buried wastes
and/or soil contamination. The locations of the test pits were determined based on surface piles of debris,
staining of soil, or allegations of suspicious activities made by tribal representatives. Locations of the test
pits are presented in Figure 3.
Test pit 1 was located at the southern end of the site and was excavated in the midst of a pile of
wood and metal debris, and stained soil. Allegations from several tribal representatives indicated that Mr.
Youngstrom broke apart equipment here, including electrical transformers. The resultant waste was burned,
buried in layers, and covered with soil, and some of the debris visible on the surface of the pile did appear to
be charred. Excavation to approximately five feet below ground surface (bgs) did not reveal any buried
waste, and no readings were obtained using a photoionization detector (PID). The START collected soil
samples 96-11-0001 and duplicate 96-11-0002 from locations within the pit. The samples were collected
using a standard procedure that involved placing soil into a stainless steel bowl using a stainless steel
spoon. The spoon was then used to homogenize the soil and transfer it to sample jars.
Test pit 2 was excavated from a large pile of soil located approximately 150 feet north of Test pit 1.
This pile also included pieces of wood and sawdust. Again, no visible signs of contamination or readings
on the PID were observed. The START collected soil sample 96-11-0003 from a composite of 2-3
locations within the pit.
The location of Test pit 3 was adjacent to a large wood debris pile and a stockpile of abandoned,
non-functioning electrical and radiological monitoring equipment. There were also small amounts of other
junk in this area, such as several car batteries and small tubes of paint. There was also a small gravel pit
located adjacent to the debris pile. The ERCS excavated the Test pit 3 to a depth of approximately five feet
bgs, and again no visible signs of contamination and no readings on the PID were observed. Soil sample
96-11-0004 was collected by the START from 3-4 locations within the pit.
Test pit 4 was located at a second pile of soil which was similar to Test pit 2, and was excavated to
an approximate depth of four feet bgs. The location of Test pit 4 was approximately 150 feet east of Test
pit 3, and the contents consisted of a large amount of sawdust mixed with sandy soil. No readings were
obtained from the PID. The START collected soil sample 96-11-0005 from a composite of two locations
within the pile.
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Key:
® = Soil Sample Location
96-11-0012®
/X ' •
Lean-To /'
oneway / A
/ ^T\
/ <^\ Parlong^Bay/'
/ Staging/.
/ Xx . -F- .
y Tin Building
Office
Junk w/Drums
Junk
Junk w/Transformer
Containers-
/ Tin'Builcling
& ' '
^ /
+ ' o
Workshop
/
tS>
Sawhouse
-v+O/s
^
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Test pits 5 and 6 were excavated from the north and south ends, respectively, of the rectangular
trench located just south of the buildings. From the amount of gravel in the bottom, this trench had
apparently been a gravel pit; however, lumber along its edges seemed to indicate that it may have also been
used as a drip pad during wood treatment operations. Both test pits were excavated to an approximate
depth of 5 feet bgs, during which no stained soil, buried waste, or readings on the PID were observed. The
START collected soil samples 96-11-0006 and 96-11-0007 from two locations in Test pit 5.
The START collected seven additional soil samples at other locations, also selected because of
possible soil contamination or allegations. Soil samples 96-11-0008 and 96-11-0009 were collected from
the northeast and southeast corners, respectively, of the sawhouse located just south of the office building.
A large amount of sawdust was deposited here when the site was active, and tribal representatives alleged
that Mr. Youngstrom performed wood treating operations along this side of the building. The START
pushed aside approximately one foot of sawdust and then used a stainless steel spoon to dig to a depth of
approximately six inches. Soil from this depth was then transferred into a stainless steel bowl, homoge-
nized, and placed into the sample jar.
Soil sample 96-11-0010 was collected from a small area of stained soil and no vegetation adjacent
to a low area in the middle of the site. The sample was collected using the previously described procedures
from an approximate depth of 12 inches. Soil sample 96-11-0011 was then collected in the low area itself,
after pushing aside approximately 12 inches of sawdust. This low area appears to have been excavated,
possibly for gravel quarrying. However, there is a small trench leading from an adjacent building into the
low area which may indicate that the location was used for the disposal of materials.
Background soil sample 96-11-0012 was collected at the extreme northern end of the site in an
apparently undisturbed location, and in the same manner as the previous samples. Next, soil samples 96-
11-0013 and duplicate 96-11-0014 were collected at the southern end of the site, along the eastern fence
line adjacent to the cigarette shop. The sample was collected at approximately 10 inches bgs using the same
sampling procedures. A previously conducted survey with a metal detector had indicated that there was
some type of buried metal in this area.
All 14 samples were analyzed in the field for pentachlorophenol (PCP) using immunoassay test kits.
None of the sample results exceeded the method detection limit of 0.1 mg/kg. Information on the test kits
and analytical results is provided in Appendix G.
Based on the results of the sample analyses, the OSC decided that further investigation of these
areas was not warranted.
3.5 Other Wastes
Other potential sources of contamination were also addressed during the removal action. Four
oxygen-generating canisters were discovered, overpacked, and staged with the containers as a separate
wastestream. The car batteries were re-staged and eventually recycled by a local business. Several vats and
open tanks located at the southwest corner of the property were visually investigated. These were allegedly
used by Mr. Youngstrom for wood treating purposes and their contents were disposed of onto the ground at
the south end of the site. Upon inspection, the vats were empty and in sound condition, and there was no
visual staining of the ground around them.
In addition, the START made a complete inventory of the electrical and radiological monitoring
equipment present on site. Information was taken from serial plates and covers, and consisted of the
following:
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G Victoreen Instrument Company, Cleveland, Ohio
Logarithmic Count Rate Meter, Model 727
G Jordan Electronics, Alhambra, California
Model AGB 500-SR, Serial # 80C
G Atomic Instrument Company, Cambridge, Massachusetts
Counting Rate Monitor
G John Fluke Mfg. Co., Inc., Seattle, Washington
High Voltage DC Supply, Model 410A, Serial #134
Property of U.S. Atomic Energy Comission
G Leeds Northrup, Philadelphia, Pennsylvania
Synchronous Motor LIN# 17-2-0-30, 115 volts, 1 phase, 60 cycles, 1800 rpm
Motor manufactured by General Electric, Schenectady, New York
G Cannon Electric Co., Los Angeles, California
G Josam Mfg. Co., Michigan City, Indiana
HydroPnuematic Action Absorbotron Shock Absorber
G Foxboro Company, Foxboro, Massachusetts
Temperature Transmitter, Type 12A, Serial # 875086
G Consolidated Electrodynamics Corp., Pasadena, California
G Natural Lighting Corp., Burbank, California
Colortron Superior Model Graphic Arts Converter, Serial # CSU93A-6E
G Allis-Chalmers, Milwaukee, Wisconsin
5/8 % JFR Voltage Regulator, Serial # 9-0110-00162-273
G Square D Company, Los Angeles, California
Voltage Control Circuits
G Lincoln Electric Company, Cleveland, Ohio
Shield Arc Welder Type SAE 300, 40 volts, 300 amps, Serial # A10-0398
G Westinghouse Corporation
Life-line Starter, Class 11-200N, Type N, Size 0
G General Electric Co., Schenectady, New York
Single Phase, Additive Polarity Electrical Transformer #6968876
3.6 Final Waste Disposition
Once all potential sources and areas of contamination had been investigated and addressed,
arrangements were made for the off-site disposal of the wastestreams. This included investigation-derived
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waste such as spent protective clothing, visqueen, and hazcat waste. Appendix H contains copies of the
Uniform Hazardous Waste Manifests. The various wastestreams and volumes, as well as the disposal
facility they were transported to are:
Envirosafe Services of Idaho, Inc.
Grandview, Idaho
Sodium Hydroxide, solid, (1) 55-gallon drum, 200 pounds
Hazardous waste, liquid, n.o.s. (Oil), D008, (10) 55-gallon drums, 550 gallons
Asbestos, (1) 55-gallon drum, 500 pounds
Non-regulated grease, (3) 55-gallon drums and (2) 85-gallon overpacks, 200 gallons
Waste Environmentally hazardous substances, solid, n.o.s. (D008), 35 cubic yards
Non-regulated sand, 22,000 pounds
Aptus Rollins OPC
Aragonite, Utah
Waste paint-related materials, D001, D007, D008, F002, F003, (2) 55-gallon drums, 300
pounds
Waste paint-related materials, D001, D006, D007, D008, F002, F003, (43) 55-gallon drums,
13,500 pounds
Tars, Liquid, D001, (19) 55-gallons drums and (5) 85-gallon overpacks, 8,400 pounds
Potassium peroxide, D003, D005, (4) 5-gallon lab packs, 6 pounds
4.0 COST SUMMARY
The costs required to accomplish the activities undertaken during the removal action are summa-
rized below.
Established
Estimated Costs
Ceilinss
Through January 31. 1997
ERCS
$250,000
$106,233
START
$ 40,000
$ 33,850
EPA
$ 20,000
$ 5,500
Contingency
$ 27,000
--
Total Project Costs
$337,000
$145,583
5.0 CONCLUSIONS
The EPA conducted a removal action at the Youngstrom Log Home site in order to address
unsecured containers with unknown contents. The removal action included sampling and categorizing the
container contents, identifying wastestreams, bulking the contents according to wastestream, and removing
the waste off site for proper disposal. Over 1,000 containers of various sizes were addressed in this
manner, and were eventually disposed of in 10 separate wastestreams.
The removal action also addressed other potential areas of concern, including soil contamination and
piles of junk and debris. Through visual examination, soil excavation, and the collection and analysis of
samples, the EPA was able to determine that there were no other hazards present on site requiring
immediate attention.
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REFERENCES
Ecology and Environment, Inc., (E & E), 1992, Site Assessment Final Report for Youngstrom Log
Homes. Blackfoot. Idaho. Techncal Assistance Team, TDD T10-9110-019. Prepared for the U.S.
Environmental Protection Agency, Superfund Response and Investigations Section, Region X,
Seattle, Washington.
, 1996, Quality Assurance Sampling Plan for Youngstrom Log Homes. Blackfoot. Idaho. Superfund
Technical Assessment and Response Team, TDD 96-10-0006. Prepared for the U.S. Environmental
Protection Agency, Environmental Clean-up Office, Region 10, Seattle, Washington.
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APPENDIX A
U.S. EPA REMOVAL SITE ASSESSMENT REPORT
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September 22, 1992
Chris D. Field
U.S. Environmental Protection Agency
1200 Sixth Avenue, HW-113
Seattle, WA 98101
Ref: TDD T10-9110-019
Dear Chris:
Enclosed please find a copy of the site assessment report and the Potential Hazardous Waste
Identification form for the Youngstrom Log Homes site in Blackfoot, Idaho. Field work was
conducted from April 7, 1992 to April 9, 1992. During the assessment TAT noted the presence of
approxmately 100 containers ranging in size from one to 55 gallons. Most of these containers are
arranged in piles and are in poor condition from weathering. Leakage and/or spillage onto the ground
was noted in several places. Several large piles of wood and metal debris, as well as scattered
batteries, electrical transformers, and military supplies, were also noted.
Sixteen samples were taken from containers of varying sizes. Based on the results of field
screening tests, seven of the samples were submitted for laboratory analysis. Results revealed mostly
BNAs and heavy metals, including 4,800 mg/kg of 2-methylnaphthalene and 345,000 mg/kg of zinc.
In addition, nine soil samples and one groundwater sample were also collected for laboratory analysis.
The soil samples were collected primarily from around leaking containers, while the groundwater
sample was collected from an on-site well. Soil sample results revealed a wide array of contaminants,
such as 179 mg/kg of lead, 14,000 mg/kg of pentachlorophenol, and an estimated 95 g/kg of
beta-BHC. Analysis of groundwater samples revealed two heavy metals, lead and zinc, both at
concentrations below primary and secondary MCLs.
Based on site conditions and the sample analysis results the primary threats the site poses are
to soil contamination and direct contact with on-site containers and soil. It is recommended that the
site warrants further consideration for a removal action to relieve these threats, possibly including
overpacking the weathered drums and the excavation of contaminated soils. Both soil and containers
could be placed inside one of the on-site buildings for temporary storage until off-site removal and
disposal, and cost responsibility issues can be resolved.
Sincerely,
William L. Carberry
Technical Assistance Team Leader
JTK/thl
Enclosure
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Ecology and Environment, Inc. - Technical Assistance Team
Document Circulation Request
TO: William Carberry, TATL, E & E, Seattle
FROM: , OSC
SUB J: Youngstrom Log Homes Site Assessment Report
REF: T10-9110-019
Please mail copies of the above-noted report to the following parties:
Name Address Date Sent (TAT)
OSC
-------
TECHNICAL ASSISTANCE TEAM
SITE ASSESSMENT
FINAL REPORT FOR:
YOUNGSTROM LOG HOMES
BLACKFOOT, IDAHO
TDD T10-9110-019
REPORT PREPARED BY: ECOLOGY AND ENVIRONMENT, INC.
PROJECT MANAGER: JERYL T. KOLB
DATE: SEPTEMBER, 1992
SUBMITTED TO CHRIS D. FIELD, DEPUTY PROJECT OFFICER
SUPERFUND RESPONSE AND INVESTIGATIONS SECTION
U.S. ENVIRONMENTAL PROTECTION AGENCY
REGION X
SEATTLE, WASHINGTON
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ABSTRACT
The Youngstrom Log Homes site is an abandoned sawmill and fabricated log home
construction facility located within the Fort Hall Indian Reservation near Blackfoot, Idaho.
While in operation, large amounts of scrap material were accepted for disposal on the
property. This material varied from scrap wood and metal to car batteries and electrical
transformers. Approximately 500 containers ranging in size from one to 55-gallons were
also accepted for storage at the site.
At the request of the U.S. Environmental Protection Agency, Ecology and Environment,
Inc. Technical Assistance Team (TAT) conducted site assessment activities at the site on
April 7-8, 1992. The assessment included written and photodocumentation of site
conditions, including an inventory of the containers.
TAT also collected samples from sixteen of the containers. These samples were tested
in the field and based on results, seven were sent to a commercial laboratory for further
analysis. Those results revealed a wide range of concentrations of volatile organic
compounds, base/neutral/acid extractable organic compounds (BNAs), pesticides, and
heavy metals. Concentrations ranged from 0.28 mg/kg of lead to 41,000 mg/L of total
xylenes.
TAT also collected nine soil samples and two groundwater samples, including one field
blank. Elevated levels of BNAs and heavy metals were detected in the soil samples, with
concentrations ranging from 14,000 mg/kg of pentachlorophenol to 0.04 mg/kg of mercury.
The groundwater samples contained detectable concentrations of lead and zinc, both of
which were below primary and secondary Maximum Contaminant Levels.
Based on site conditions and the results from sample analysis, the threats the site may
pose are to soil contamination and direct contact with the containers and contaminated soil.
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TABLE OF CONTENTS
Section Page
ABSTRACT
1.0 INTRODUCTION 1
2.0 SITE CONDITIONS AND BACKGROUND 1
2.1 Site Description 1
2.1.1 Site Evaluation 1
2.1.2 Site Location 2
2.1.3 Site Characteristics 2
2.1.4 Release Threat Posed By Site 2
2.1.5 NPL Status 5
2.2 Actions to Date 5
2.2.1 Previous Actions and Investigations 5
2.2.2 Current Action 5
2.2.2.1 Sampling Rationale 6
2.2.2.2 Sampling Results 6
3.0 PUBLIC HEALTH AND ENVIRONMENTAL THREATS 11
3.1 Threats to Public Health and Welfare 11
3.2 Threats to the Environment 11
4.0 ENDANGERMENT DETERMINATION 14
5.0 ACTION ALTERNATIVES 14
6.0 CONCLUSIONS 14
REFERENCES
APPENDIX A: PHOTOGRAPHIC DOCUMENTATION
APPENDIX B: DATA QUALITY ASSURANCE REVIEW AND ANALYTICAL
SUMMARY SHEETS
APPENDIX C: ON-SITE CONTAINER AND JUNK PILE INVENTORY
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LIST OF FIGURES
Figures Page
1 Site Location Map 3
2 Site Map 4
3 Container Sample Locations 7
4 Soil and Groundwater Sample Locations 9
LIST OF TABLES
Tables Page
1 Container Sample Field Screening Results 8
2 Container Sample Analytical Results 10
3 Soil Sample Analytical Results 12
4 Groundwater Sample Analytical Results 13
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SITE ASSESSMENT REPORT FOR
Youngstrom Log Homes
Blackfoot, Idaho
T10-9110-019
Site Name/Address :
Youngstrom Log Homes
P.O. Box 356
Blackfoot, ID 83221
Investigation Participants :
Jeryl Kolb, TAT-Project Manager
Jill Roberts, TAT
Charlie Granda, TAT
MarkWoodke, TAT
Ecology and Environment, Inc., Seattle, Washington
206/624-9537
Dates of Site Assessment :
April 7-9, 1992
1.0 INTRODUCTION
The Environmental Protection Agency (EPA) Region X Superfund Response and
Investigations Section (SRIS) tasked the Ecology and Environment, Inc., (E & E) Region
10 Technical Assistance Team (TAT) to conduct an assessment at the Youngstrom Log
Homes (Youngstrom) site in Blackfoot, Idaho.
The Youngstrom site was brought to the EPA's attention during a Resource
Conservation and Recovery Act (RCRA) compliance inspection conducted by EPA officials
from the Idaho Operations Office in 1991. The inspection noted that the facility was
abandoned and contained numerous stockpiled 1-, 5-, and 55-gallon size containers, most of
which were full or partially full and in poor condition.
The EPA tasked TAT to conduct a site assessment to determine the contents of the
containers, evaluate the threat they pose to public health and the environment, identify
migration targets, and determine the need for a removal action at the site.
1
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2.0
SITE CONDITIONS AND BACKGROUND
2.1 Site Description
2.1.1 Site Evaluation
The Youngstrom Log Homes site is a former sawmill and fabricated log home
construction facility. The property is located on the Fort Hall Indian Reservation and was
leased by Lewis Youngstrom from the Shoshone-Bannock tribe. The lease was apparently
revoked in 1987 and the property abandoned.
The tribal representative, Roger Turner, met with TAT prior to the assessment. He
stated that the entire site is fenced and that the gate is locked. However, the fence is a split
log type, and with the presence of abandoned machinery on site, trespassing, vandalism, and
robbery are problems. Turner gave TAT keys to the gate and notified local law
enforcement officials that TAT had permission to be on the property.
2.1.2 Site Location
The Youngstrom site lies completely within the Fort Hall Indian Reservation,
approximately 6 miles south of Blackfoot, Bingham County, Idaho (Figure 1). The site is
located on the north side of State Highway 91 approximately 1/2 mile southwest of
Interstate 15, within section 20, Township 3 South, Range 35 East.
The surrounding area is predominantly agricultural in use, with scattered homes and
businesses. The closest residence is approximately 150 yards northeast of the site. The
North Canal, an agricultural irrigation canal, forms the northern and eastern boundaries of
the site, Highway 91 the southern boundary, and farm fields the western boundary.
2.1.3 Site Characteristics
The Youngstrom site was leased from the Shoshone-Bannock Tribes by Lewis
Youngstrom, who used the property to operate his fabricated log home construction
business. It is not known what date operations were started, but the lease was revoked by
the tribe in 1987, and Youngstrom abandoned the site at that time. Youngstrom also
operated a sawmill and accepted liquid and solid waste from third parties, but allegedly did
not conduct wood treatment operations on the site.
The site contains approximately 20 buildings, numerous junk piles, stockpiles of
containers, abandoned vehicles, and two shallow trenches or pits (Figure 2). The majority
of the buildings contain sawmill machinery, tools, supplies, or materials, however several of
the smaller open shell buildings are empty.
The containers range in size from 1- to 55-gallons. Most are either full or partially
2
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full and are in poor condition. Most do not have identifying labels on them. Areas of
spillage or leakage are apparent around several of the stockpiles.
2.1.4 Release Threat Posed By Site
There are several targets threatened by a potential release from this site. Soil
contamination is possible due to leaking drums and other containers present. Areas of
spillage or leakage have been observed. In addition, the junk piles do contain car batteries
and electrical transformers that may also be leaking.
3
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figure 1
4
-------
figure 2
5
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Groundwater contamination is a possibility if soil contamination is widespread.
Water table conditions in the vicinity of the site are fairly shallow, however agricultural and
drinking water wells utilize water from deeper artesian aquifers confined by an intervening
clay layer (USDA 1977, USGS 1984).
While the site is not situated in a heavily populated area, direct contact between
contaminants and the public is possible. The area is not properly fenced and is attractive to
vandals and scavengers due to the presence of scrap metal, machinery, and other material.
Tribal representatives told TAT they often receive calls concerning trespassing or looting.
Surface water does not appear to be seriously threatened. The North Canal is
separated from the site by a 2- to 4-foot berm, which would effectively preventing any
overland flow of contaminants.
Similarly, air contamination is not a major threat. Vegetation covers most of the
site, helping to hold down possibly contaminated soils from being blown off site.
2.1.5 NPL Status
The Youngstrom site is not listed on the NPL and no Hazard Ranking System score
has been generated.
2.2 Actions to Date
2.2.1 Previous Actions and Investigations
On April 13, 1990 Roger Turner and Gary McRae of the Shoshone-Bannock Tribe
conducted a walk-through assessment of the site. According to Turner and McRae, the
tribe conducted a comprehensive chemical inventory of the containers found at the site in
May 1990. No analytical samples were collected.
Michael Silverman and Mark Maserik of EPA, along with Constance Albright
representing the Shoshone-Bannock Tribes, conducted a RCRA Compliance Inspection on
April 2, 1991. This inspection also consisted of a walk-through assessment, along with
photo documentation. No analytical samples were collected.
An effort was made by EPA to identify the responsible party and to ascertain from
them additional information concerning site operations and waste disposal. As Lewis
Youngstrom had passed away since the site was abandoned, his son Lynn Youngstrom was
contacted. Youngstrom knew very little about site operations or the types and quantities of
waste brought to the site.
6
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2.2.2 Current Action
In conducting a site assessment of the Youngstrom site, TAT conducted photo and
written documentation of current site conditions prior to sampling activities. A
walk-through of the site was made, noting the numbers, types, and condition of the
containers, the contents of the junk piles and buildings, and the location of the on-site well.
Potential sampling locations were also noted. Photodocumentation of the site and of the
TAT sampling effort is presented in Appendix A.
2.2.2.1 Sampling Rationale
The TAT collected 16 samples from containers located on site on April 7, 1992
(Figure 3). The containers varied in size from 55-gallon to 5-gallon. Based on the results
of the field screening kits (Sensidyne Hazard Categorization and Dexsil Chlor-n-Oil) (Table
1), the number of samples submitted for chemical analysis was reduced to 7. The samples
were analyzed for parameters based on the field screening results, and included volatile
organic compounds (VOCs), base/neutral/acid extractable organic compounds (BNAs), and
polychlorinated biphenyls (PCBs).
Containers from each of the stockpiles were chosen for sampling based on the
amount of sample material available, the structural integrity of the container (or lack
thereof), and if the sample material visibly differed from that in other containers.
TAT collected 8 on-site soil samples on April 8, 1992 (Figure 4). One off-site
background soil sample was collected on April 9, 1992. The locations of the samples
collected were based around the container stockpiles and the junk piles. Areas specifically
targeted were the ground beneath containers with poor integrity, spilled transformers,
battery piles, and areas of stained soil and/or no vegetation.
All soil samples were analyzed for VOCs, BNAs, and priority pollutant metals.
Based on the locations they were collected from, 3 of the soil samples were field screened
for PCBs using Ensys immuno-assay test kits and based on those results, two of the samples
were also analyzed for PCBs by the designated laboratory.
The TAT also collected 1 groundwater sample from the on-site well on April 8,
1992. Because the well is equipped with a submersible pump, TAT was not able to
determine depth to groundwater or the depth of the screened interval. TAT sampled from
the well by restoring electrical power to the well pump through the use of a generator. Due
to the unknown depth of the well, purging was conducted for 1/2 hour. A field blank of
distilled water was also collected. Both samples were analyzed for VOCs, BNAs, PCBs,
and priority pollutant metals.
7
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2.2.2.2 Sampling Results
Container sample T2030220 contained the largest number of contaminants, in part
because both the solid and liquid phases of the sample were analyzed (Table 2). The solid
phase of the sample displayed the highest concentrations of BNAs found in any container
sample, with 4,800 mg/kg of 2-methylnaphthalene. T2030233 contained the highest
concentrations of volatile organics and pesticides, with 41,000 mg/L of total xylenes and
1,700 %/kg of endrin. Sample T2030231 contained
8
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figure 3
9
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table 1
10
-------
figure 4
11
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table 2
12
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345,000 mg/kg of zinc, the highest concentration of metals in any of the samples.
For soil sample analysis, T2030239 contained the greatest number of contaminants,
consisting of primarily BNAs and heavy metals (Table 3). Sample T2030238 contained the
highest concentration of volatile and BNA organics, with 620
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table 3
15
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table 4
16
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The State of Idaho does not currently have numerical clean-up standards for soil or
groundwater. Comparison to background levels is therefore often used to determine
elevated levels of contaminants.
4.0 ENDANGERMENT DETERMINATION
The Youngstrom site does not appear to pose an imminent threat either to public
health and welfare, or to the environment. Present
site conditions do warrant concern, however. Many of the containers on site are exposed to
the elements and have poor structural integrity. Leaking of contents onto the ground was
observed by TAT. Soil and groundwater contamination is present, however geological
conditions in the area would seem to indicate that the threat to groundwater is minimal.
The upper aquifer is not used for drinking or irrigation purposes, and the lower aquifer is
confined by a thick clay layer. Similarly, the threat to surface water is small due to the
higher terrain located between the site and the closest surface water body, in this case the
North Canal.
The primary threats the site poses then are to soil contamination from leaking
containers and direct contact with materials stored in containers or with contaminated soil.
5.0 ACTION ALTERNATIVES
TAT recommends that the on-site containers be transferred to overpacks and then
placed inside one of the secure buildings that exist on site for temporary storage. During
the assessment TAT noted several buildings with concrete floors, intact walls and roofs, and
no windows. By placing the containers inside the building and securing it, imminent threats
to any trespassers and to further soil contamination would be solved. Contaminated soil
would be excavated from beneath and around the containers and also placed inside one of
the buildings. Adequate fencing to prevent trespassing should also be placed around areas
where hazards have been confined.
Containers and soil could be temporarily stored in on-site buildings, thereby
mitigating imminent threats posed by the site while EPA and the responsible parties
negotiate dispose of the wastes.
6.0 CONCLUSIONS
The Youngstrom Log Homes site is an abandoned prefabricated log home
construction facility in Blackfoot, Idaho. While in operation the site owner also accepted
large amounts of scrap and waste for disposal on the property. This includes approximately
500 containers ranging in size from 1- to 55-gallons. Most of these containers are in poor
condition, with few identifying markings. Areas of spillage of leakage are apparent.
During site assessment activities TAT collected samples from 16 containers. These
17
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samples were tested in the field and, based on the results, were reduced to seven composites
which were submitted to a commercial laboratory. TAT also collected nine soil samples,
including one off- site background sample, and one groundwater sample. Most of the soil
samples were collected from soil around and beneath containers. The groundwater sample
was collected from an on-site well.
Sample results revealed elevated levels of contaminants in both the container and
soil samples. Most of the contaminants were BNAs or heavy metals. Based on site
conditions and sample analysis results, the site may pose a direct contact threat. This is
based on the accessibility of the site, past incidences of vandalism, the condition of the
containers, and the levels of contaminants detected in soil and container samples.
18
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REFERENCES
Kolb, Jeryl, 1992, Technical Assistance Team Sampling Plan For: Youngstrom Log Homes
Site. Ecology and Environment, Inc., Seattle, WA.
U.S. Dept. of Agriculture, 1977, Soil Survey of Fort Hall Area. Idaho Parts of Bannock-
Bingham. Caribou, and Power Counties. Soil Conservation Service in cooperation
with University of Idaho College of Agriculture.
U.S. Geological Survey, 1984, Hydrogeologv of Eastern Michaud Flats. Fort Hall Indian
Reservation. Idaho. Water Resources Investigations Report 84-4201, prepared in
cooperation with the Shoshone-Bannock Tribes, Fort Hall Indian Reservation.
40 CFR 141.11, National Primary Drinking Water Regulations. Maximum contaminant
levels for inorganic chemicals.
40 CFR 143.3, National Secondary Drinking Water Regulations. Secondary maximum
contaminant levels.
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APPENDIX A
PHOTOGRAPHIC DOCUL1EIITATIION
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PHOTOGRAPH IDENTIFICATION SHEET
Camera Serial No.: 646171 TDD No.: T10-9110-019
Lens Type: 35 mm Site Name: Youngstrom Log Homes
Phot
o No.
Date
Time
Taken By
Description
1
4/9/92
0830
Kolb
Office building with company sign.
2
4/7/92
1115
Kolb
Several on-site buildings.
3
4/8/92
1045
Kolb
Junk pile with open transformer visible in the
middle on the photo.
4
4/7/92
1110
Kolb
Abandoned vehicles on site. Container stockpile is
to the right.
5
4/7/92
1120
Kolb
5-gallon containers. Label reads "Aluminum Heat
Resisting Paint".
6
4/7/92
1120
Kolb
Another contianer stockpile. Several labels reads
"Bitumastic Jet Set Primer".
7
4/8/92
1015
Kolb
Batteries located on large junk pile.
8
4/7/92
1050
Kolb
Container stockpile located at the far southwest
corner of the site.
9
4/7/92
1450
Kolb
Collecting container sample T2030222 from 55-
gallon drum.
10
4/7/92
1520
Kolb
Collecting container sample T2030227 from a 5-
gallon pail.
11
4/7/92
1540
Kolb
Preparing to collect container sample T2030229.
12
4/7/92
1620
Kolb
Collecting container sample T2030233 from a 5-
gallon pail.
13
4/7/92
1630
Kolb
Collecting container sample T2030234 from a 55-
gallon drum of oil.
14
4/8/92
0940
Kolb
Collecting soil sample T2030236. Edge of the
gravel pit is visible.
15
4/8/92
0955
Kolb
Collecting soil sample T2030237.
16
4/8/92
1030
Kolb
Collecting soil sample T2030240 from
unvegetated area near oil drums.
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PHOTOGRAPH IDENTIFICATION SHEET
Camera Serial No.: 646171 TDD No.: T10-9110-019
Lens Type: 35 mm Site Name: Youngstrom Log Homes
Phot
o No.
Date
Time
Taken By
Description
17
4/8/92
1045
Kolb
Collecting soil sample T2030243 from white
material emptied from transformer. Transormer
lid is visible to the upper left of the pile.
18
4/8/92
1050
Kolb
Junk pile from which soil sample T2030242 was
collected.
19
4/8/92
1110
Kolb
Field screening samples inside the large on-site tin
building.
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APPENDIX B
DATA QUALITY ASSURANCE REVIEW
¦ "L SUMMARY SHEETS
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APPENDIX C
ON-SITE CONTAINER AND JUNE PILE INVENTORY
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First Container Stockpile (corresponds to samples T2030220-225)
46 55-gallon drums (22 full or partially full)
3 30-gallon drums (all full)
33 5-gallon pails (all full)
Second Container Stockpile (corresponds to samples T2030226-227)
24 5-gallon pails (labeled "Houghton-Draw")
33 55-gallon drums (mostly empty; some contain solidified tar)
18 5-gallon pails (all empty)
1 25-gallon drum (full and sealed, no markings)
Third Container Stockpile (corresponds to samples T2030228-231)
300 5-gallon pails (stacked on pallets, full or partially full,
some labeled "carbo-zinc")
Fourth Container Stockpile (corresponds to samples T2030232-233)
74 5-gallon pails (sealed or partially open, some leakage,
most labeled "Aluminum Heat Resisting Paint")
-200 1-gallon cans (placed on pallets, no markings, most are
leaking)
First Junk Pile
Consists of scattered wood debris, soil, numerous tires, 10-15 car
batteries, 6 empty 55-gallon drums, -100 empty 1-gallons cans, a
1000-gallon tank, and a small pile of military Geiger counters.
Second Junk Pile
Consists of piled soil, wood and rusty metal, tires, one open
electrical transformer, and two empty 55-gallon drums.
Third Junk Pile
Consists of piled dirt and wood, - 50 empty 55-gallon drums, and
rusty scrap metal.
Fourth Junk Pile
Consists of piled dirt and wood, 5 empty 55-gallon drums, and an
electrical transformer lid.
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Fifth Junk Pile
Consists of piled dirt and wood, 6 empty 55-gallon drums.
There are also 4-5 smaller piles consisting of wood and rusty metal, as
well as scattered empty 55-gallon drums.
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APPENDIX B
ACTION MEMORANDUM
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. *
UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
REGION 10
1200 Sixth Avenue
Seattle, Washington 98101
MEMORANDUM
DATE:
SUBJECT:
TO:
FROM:
THROUGH:
September 26, 1996
Request for a Removal Action at
Youngstrom Log homes, in Bingham County,
Blackfoot, Idaho
Randy M. Smith, Director,
Environmental Cleanup Office
William H. Freutel,
OSC
Lero^^^Soa^elle, Manager
ECL Cleanup Unit #1
Site ID#: 102T
ERNS #:
I. PURPOSE: The purpose of this action memorandum is to
request and document approval of the proposed removal
action for the uncontrolled waste found on the Youngstrom
Log Home in Blackfoot, Idaho. The site lies completely
within the Fort Hall Indian Reservation, on the north side
of Highway 91, approximately one-half mile southwest of
Interstate 15.
II. SITE CONDITIONS AND BACKGROUND: This is a time-critical
removal action.
A. SITE DESCRIPTION:
1. Removal Site Evaluation
The Youngstrom Log Homes site is a former sawmill
and log home construction facility. The property
was leased by Lewis Youngstrom from the Shoshone-
Bannock Tribe. The lease was revoked in 1987 and
the property was abandoned. Hundreds of drums and
containers were abandoned on-site. Many of the
drums and containers have leaked or burst open and
have contaminated the surrounding soil. There are
unconfirmed reports of buried wastes on site.
Printad on Recycled Paper
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Physical Location and Site Characteristics
The surrounding area is predominantly agricultural
in use with some nearby homes and businesses. The
closest residence is approximately 150 yards
northeast of the site. The North Canal, an
agricultural irrigation canal, forms the northern
and eastern boundaries. The south and west sides
of the site are bordered by State highway 91 and
farm fields, respectively.
Site Characteristics
The site has been abandoned since 1987. Most of
the site is fenced with a 3-rail cedar fence.
Trespassing has been a problem. It appears that
the amount of wastes on-site has increased since
EPAs 1992 assessment. The site currently contains
approximately 20 buildings, numerous junk piles,
more than 500 containers (1 gals., 5 gals, and 55
gals), abandoned vehicles, and two shallow
trenches. Most of the containers are unlabeled,
contain product, and are in poor condition.
The site is owned by the Shoshone-Bannock Indian
Tribe. The former operator of the Business, Lewis
Youngstrom, is deceased. EPA first assessed the
site in 1992 and forwarded the results to the
Shoshone-Bannock Tribe, with some recommendations
for cleanup action. The Tribe has since
determined that they do not have the financial
ability to conduct the necessary cleanup.
Release or Threatened Release into the Environment
of a Hazardous Substance, or Pollutant or
Contaminant
EPA contractors collected 16 samples from on-site
containers. Contaminants detected include
volatile, semi-volatile, pesticides, and metals,
in containers of varied size and origin. Field-
screening results indicated the presence of acids,
bases and flammable materials. Uncontrolled
flammable materials on site may pose a serious
threat of fire and explosion. In the event of a
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fire, fire fighting efforts would be greatly
impeded by the unknown nature of most of the
materials on-site.
Eight soil samples were collected from areas
around the container stockpiles and junkpiles,
targeting areas of stained-soil and stressed
vegetation. Sample results showed volatile, semi -
¦volatile, heavy metal and pesticide contamination.
One sample exhibited the highest hits of both
volatile and BNA organics with 620 parts per
billion of 2-methyl-2-pentanone and 14,000 parts
per million of pentachlorophenol, respectively.
Due to the numerous, unknown sources of the
abandoned material, these sample results may not
represent all contaminants on site- The elevated
levels of pentachlorophenol indicate that wood
treatment operations may have taken place on-site.
There are radio nuclide respirator cartridges,
Geiger counters, and other materials that indicate
that radiation may be encountered on site. .
Radiation screening has not been conducted. There
are also unconfirmed reports of unmarked burial
areas on site.
5. NFL Status: The site is not listed on the NPL.
The site has been referred to the site assessment
program for site investigation
6. Maps and other graphic representations; See the
attached location map and site diagram.
B, OTHER ACTIONS TO DATS:
1. Previous Actions:
April 1990 - Site Evaluation conducted by Roger
"Turner, Shoshone-bannock Tribal representative,
and Gary Morae
, April 1991 - EPA RCRA Compliance Inspection by
Mike Silver man and Mark Masarik.
August 1991- EPA sent Potentially Responsible
Party letter to Lewis Youngstrom (Company Owner),
Jay Youngstrom, and Lynn Youngstrom (owners sons).
Lewis Youngstrom is deceased. His survivors have
limited knowledge of the business and reportedly
limited assets.
3
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July 1991 - Bannock-Shoshone Tribal requested
assistance to Region 10 Administrator.
April 1992 - EPA conducted Removal Assessment and
forwarded the findings and Removal Recommendations
to Roger Turner.
2. Current Actions:
June 1996 - EPA was contacted by the Susan Hanson,
Shoshone-Bannock Tribal representative, regarding
the tribes inability to fund a cleanup action
estimated by consultants at $300,000. The Tribe
requested EPA assistance in mitigating site
hazards. EPA headquarters arranged' an estimated
$300,000 to fund an EPA-lead Removal action.
September 1996 - EPA On-scene Coordinator did a
site walk-through to determine current site
conditions and evaluate the need and cost for
Removal Action.
C. STATE AND LOCAL AUTHORITIES' ROLES:
1. State and Local Actions to Date: None. The site is
located on Tribal land/ no state or local
jurisdiction.
2. Potential for Continued State and Local Response:
None. This site is on Tribal land and the State
has no authority.
III. THREATS TO PUBLIC HEALTH OR WELFARE OR THE ENVIRONMENT, AND
STATUTORY AND REGULATORY AUTHORITIES:
A. THREATS TO PUBLIC HEALTH OR WELFARE:
The most likely exposure pathways to the
contaminants on site are via inhalation of
contaminated dust or fumes and/or direct contact.
Both pathways are a threat to surrounding
residents and anyone accessing the site. Dogs
from a nearby home were on the site during EPAs
recent visit. There were clear signs of recent
activity on site which could have been related to
dumping or salvaging. Many of the site
contaminants, including Pentachlorophenol and
heavy metals, pose a health threat from primary
4
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contact on site, as well as secondary contact with
materials tracked from the site. Most of the
drums and containers have not been sampled and may
present other significant threats. Radiation
screening has not been conducted despite the
presence of radiological equipment on site. Fire
and explosion hazards are also a concern due to
uncontrolled flammable and incompatible materials
on site. In the event of a fire, the down-wind
exposure risks remain largely unknown.
B. THREATS TO THE ENVIRONMENT:
Although the primary threats posed by the site
relate to public health,- contaminated soils on
site may pose a threat to shallow groundwater and
the North Canal which forms the north and west
border of the site.
IV. ENDANGERMENT DETERMINATION:
Actual or threatened release of hazardous
substances from this site, if not addressed by
implementing the response action selected in this
Action Memorandum, may present an imminent and
substantial endangerment to public health, or
welfare, or the environment.
V. PROPOSED ACTIONS AND ESTIMATED COSTS:
A. PROPOSED ACTIONS:
1. Proposed Action Description:
The Removal action will consist of: hazard
categorizing all containerized material on site.
Compatible waste streams will be consolidated and
profiled. Leaking containers will be consolidated
or overpacked. Soil contamination will be
characterized and removed. Geophysical
instrumentation may be used to
identify/investigate potential burial areas. Once
liquid and solid wastes have been consolidated and
staged, the waste streams will be prof i J ed for
disposal. Every attempt will be made to recycle
uncontaminated product identified on site.
5
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Consistent with EPAs off-site policy, potential
disposal facilities will be checked for compliance
status. EPA and the tribe will take steps to
secure the site to prevent future dumping of
hazardous materials.
2. Contribution to remedial performance
If the Removal' Action proposed herein is approved
and implemented, no further remedial action will
be required.
3. Description of alternative technologies
EPA will make every effort to recycle products
that are of value.
4. EE/CA: N/A
5. Applicable or relevant and appropriate
requirements (ARARS)
Federal and State ARARs will be considered and met
to -the extent practicable.
6. Project Schedule
Response activities can begin during October 1996
and the proposed action will require approximately
30 to 45 days to completion.
6
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B. ESTIMATED COST
Extramural Costs:
Regional Allowance Costs:
Total Cleanup Contractor Costs $250, 000.
Other Extramural Costs:
Total TAT costs $40,000
Total NCLP
Total REAC
Subtotal, Extramural Costs $290,000
Extramural Costs Contingency(10%) $ 27,000
TOTAL, EXTRAMURAL COSTS $317,000
Intramural Costs:
Intramural Direct Costs $ 15,000
Intramural Indirect Costs $ 5,000
TOTAL, INTRAMURAL COSTS $ 20,000
TOTAL REMOVAL PROJECT CEILING $337,000
VI. EXPECTED CHANGE IN THE SITUATION SHOULD ACTION BE DELAYED
OR NOT TAKEN:
If the proposed action is denied or delayed the
situation on site will continue to deteriorate.
Leaking containers will further contaminate the
surrounding soil and threaten shallow groundwater.
Uncontrolled site access may continue posing known and
unknown health risks to" anyone entering the site. The
fire and explosion hazard may increase due to continued
deterioration and\or vandalism.
VII. OUTSTANDING POLICY ISSUES: None
7
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VIII. ENFORCEMENT;
According to the Shoshone-Bannock Tribal Council, the
Tribal government was the entity that leased the land
to Lewis Youngstrom. Under CERCLA 107, Tribal
governments are not a "person", and therefore not
liable for reimbursement. Therefore, there is no cost
recovery planned against the Tribe. Past investigation
of Lewis.Youngstrom' (deceased), and his survivors,
indicate limited financial viability, thus no cost
recovery actions are planned against them.
EPA will notify and hold liable, the Department of
"Energy-(DOE), for all costs associated with the .
handling and disposal of hazardous materials
originating from DOE sites.
This decision document represents the selected removal
action for the Youngstrom Log Homes site in Blackfoot,
Idaho, developed in accordance with CERCLA as amended,
and not inconsistent with the NCP. This decision is
based on .the administrative record for the Conditions
at the' site meet the NCP section 300.415(b)(2) criteria
for removal and I recommend your approval of the
proposed removal action. The total project ceiling if
approved will be $337,000. The entire amount will be
funded by EPA headquarters.
IX. RECOMMENDATION:
(Approval)
(Disapproval)
8
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YOUNGSTROM LOG HOMES SITE
BLACKFOOT, IDAHO
-------
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YOUNGSTROM LOG HOMES SITE
BLACKFOOT, IDAHO
-------
APPENDIX C
SITE PHOTOGRAPHS
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PHOTOGRAPH IDENTIFICATION SHEET
Camera Serial #: 645489 TDD #: 96-10-0006
Lens Type: 30-70 mm Site Name: Youngstrom Log Homes
Photo No.
Date
Time
By
Description
1.01
10/29/96
1230
J. Kolb
View of site looking north from empty fuel tank.
1.02
10/29/96
1233
J. Kolb
Stockpile of 55-gallon drums.
1.06
10/29/96
1242
J. Kolb
55-gallon drum labeled "Steam turbine lube oil".
1.09
10/29/96
1250
J. Kolb
View of site looking northeast from atop the canal dike.
1.10
10/29/96
1250
J. Kolb
Stockpile of various-sized containers.
1.16
10/29/96
1312
J. Kolb
View of site looking south from office building towards the saw-
mill building.
1.19
10/29/96
1320
J. Kolb
View of office building and business sign.
1.21
11/7/96
1015
J. Kolb
ERCS using bulldozer to scrape and level area in front of office
building.
2.01
11/7/96
1515
J. Kolb
ERCS using truck to move first load of containers from south end
of site to staging area in parking bays.
2.05
11/7/96
1628
J. Kolb
Staging containers on visqueen using forklift.
2.06
11/7/96
1631
J. Kolb
View of the contents of one open 5-gallon container.
2.09
11/8/96
0805
J. Kolb
View of south end of site with new roads and stockpiled containers
ready for moving.
2.11
11/8/96
1130
J. Kolb
Opening, numbering, and inventorying staged containers in prepa-
ration for sampling
2.17
11/8/96
1418
J. Kolb
Numbering and opening staged containers under the lean-to.
2.18
11/8/96
1435
J. Kolb
START hazcat station at north end of parking bays.
2.19
11/8/96
1545
J. Kolb
Continuing to number and open staged containers under lean-to.
2.23
11/8/96
1715
J. Kolb
START hazcatting samples; note flame test on copper wire.
3.01
11/9/96
0900
J. Kolb
ERCS staging empty containers west of office building.
3.02
11/9/96
0933
J. Kolb
START in Level B collecting samples from containers under the
lean-to.
3.08
11/9/96
1030
J. Kolb
ERCS preparing to stage 55-gallon containers at prepared area
west of the lean-to.
3.12
11/9/96
1640
J. Kolb
View of remaining sampled containers under parking bay. These
are one wastestream.
3.15
11/10/96
1345
J. Kolb
View of the second staging area west of the office building being
used to stage sampled containers according to wastestream.
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PHOTOGRAPH IDENTIFICATION SHEET
Camera Serial #: 645489 TDD #: 96-10-0006
Lens Type: 30-70 mm Site Name: Youngstrom Log Homes
Photo No.
Date
Time
By
Description
3.16
11/11/96
1045
J. Kolb
View of first parking bay with smaller containers staged in front of
it for sampling.
3.20
11/11/96
1517
J. Kolb
START in Level B, hazcatting contents directly from the contain-
ers.
3.22
11/11/96
1555
J. Kolb
START in Level B, hazcatting contents directly from the contain-
ers.
4.09
11/12/96
1103
J. Kolb
START hazcatting the contents of the remaining containers di-
rectly from the containers at two separate stations.
4.10
11/12/96
1305
J. Kolb
ERCS using backhoe to crush empty 55-gallon drums for off-site
disposal.
4.12
11/13/96
0806
C. Kitz
ERCS using backhoe to excavate Test pit 1 at the south end of the
site near the empty vats.
4.14
11/13/96
0812
C. Kitz
ERCS excavating Test pit 2 along the west property line.
5.01
11/13/96
0845
J. Kolb
ERCS excavating Test pit 5 at the north end of the long rectangu-
lar trench just south of the buildings.
5.02
11/13/96
0845
J. Kolb
View of soil in Test pit 5. Consisted of sandy gravel.
5.07
11/13/96
0905
J. Kolb
View of stained soil in Test pit 1.
5.08
11/13/96
0905
J. Kolb
View of sample 96-11-0001 location in Test pit 1.
5.09
11/13/96
0905
J. Kolb
View of sample 96-11-0002 location in Test pit 1.
5.11
11/13/96
0917
J. Kolb
View of Test pit 2 where sample 96-11-0003 was collected
5.12
11/13/96
0923
J. Kolb
View of Test pit 3 adjacent to the large debris pile where sample
96-11-0004 was collected.
5.14
11/13/96
0930
J. Kolb
View of Test pit 4 where sample 96-11-0005 was collected.
5.16
11/13/96
0948
J. Kolb
View of Test pit 5 looking south, where samples 96-11-0006 and
96-11-0007 were collected.
5.20
11/14/96
0930
J. Kolb
Location of sample 96-11-0008 at northeast corner of the saw-
house.
5.22
11/14/96
0938
J. Kolb
Location of sample 96-11-0009 at southeast corner of the saw-
house.
5.23
11/14/96
0946
J. Kolb
Location of sample 96-11-0010 at stained area of soil near a low
depression.
5.25
11/14/96
0955
J. Kolb
Location of sample 96-11-0011 from within the depression.
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PHOTOGRAPH IDENTIFICATION SHEET
Camera Serial #: 645489 TDD #: 96-10-0006
Lens Type: 30-70 mm Site Name: Youngstrom Log Homes
Photo No.
Date
Time
By
Description
6.03
11/14/96
1410
J. Kolb
View of electronic equipment stockpiled on site.
6.05
11/14/96
1415
J. Kolb
Close-up view of arc welder label reads "Lincoln Electric Co.,
Shield Arc Welder".
6.07
11/14/96
1418
J. Kolb
Label reads "Square D Company, Los Angeles, California".
6.09
11/14/96
1418
J. Kolb
Label reads "Westinghouse Life-line Starter".
6.11
11/14/96
1422
J. Kolb
View of empty electrical transformer along western fence line,
looking east.
6.13
11/14/96
1423
J. Kolb
Label on transformer reads "General Electric Transformer
#6968876".
6.14
11/14/96
1435
J. Kolb
View of secondary staging area with overpacks that wastestreams
have been bulked into.
6.18
11/14/96
1455
J. Kolb
ERCS moving filled overpacks from lean-to to secondary staging
area.
7.01
11/14/96
1455
J. Kolb
View of bulking process in the lean-to area.
7.03
11/14/96
1015
J. Kolb
Location of sample 96-11-0012 from extreme north end of the
site.
7.05
11/14/96
1032
J. Kolb
Location of samples 96-11-0013 and 96-11-0014 from area at
south end of site adjacent to the Smoke Shop.
7.09
11/14/96
1045
J. Kolb
View of equipment stockpiled next to large debris pile, label reads
"Victoreen Logarithmic Count Rate Meter".
7.10
11/14/96
1045
J. Kolb
Another piece of equipment, label reads "Atomic Instrument Co.,
Counting Rate Meter".
7.12
11/14/96
1049
J. Kolb
View of electrical equipment along western fence line adjacent to
large debris pile.
7.13
11/14/96
1050
J. Kolb
View of radiation monitoring equipment.
7.15
11/14/96
1050
J. Kolb
Label reads "High Voltage DC Supply, property of U.S. Atomic
Energy Commission".
7.16
11/14/96
1052
J. Kolb
Another piece of equipment, label reads "Cannon Electric Co."
7.17
11/14/96
1053
J. Kolb
Another piece of equipment, label reads "Hydro Pneumatic Action,
Absorbotron Shock Absorber, Josam Mfg. Co.".
7.18
11/14/96
1053
J. Kolb
Another piece of equipment, label reads "Leeds Northrup Syn-
chronous Motor".
7.19
11/14/96
1055
J. Kolb
View of area next to large debris pile where equipment is located.
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PHOTOGRAPH IDENTIFICATION SHEET
Camera Serial #: 645489
Lens Type: 30-70 mm
TDD #: 96-10-0006
Site Name: Youngstrom Log Homes
Photo No.
Date
Time
By
Description
7.21
11/14/96
1057
J. Kolb
Close-up of a piece of equipment, label reads "Consolidated
Electrodynamics Corp.".
7.22
11/14/96
1057
J. Kolb
Another piece of equipment, label reads "Foxboro Temperature
Transmitter".
7.23
11/14/96
1058
J. Kolb
Another piece of equipment, label reads "Colortron Superior
Model Graphic Arts Converter, Natural Lighting Corp.".
7.24
11/14/96
1101
J. Kolb
Close-up of another piece of equipment, label reads "Allis Chal-
mers, Voltage Regulator".
8.01
11/18/96
1340
J. Kolb
ERCS moving filled overpacks into parking bays after demobili-
zation of equipment.
8.07
11/19/96
0738
J. Kolb
View of oxygen-generating canister inside poly overpack that will
be used for transport off site.
8.08
11/19/96
1035
J. Kolb
ERCS placing crushed empty drums into nonhazardous debris roll-
off box.
8.10
11/19/96
1040
J. Kolb
View of the interior of the parking bays with more overpacks
staged according to wastestream.
8.12
11/19/96
1400
J. Kolb
View inside of 5-gallon container of flammable zinc powder.
8.19
11/19/96
1610
J. Kolb
ERCS bulking 55-gallon drums of oil/water wastestream into
overpacks.
8.21
11/20/96
0740
J. Kolb
ERCS emptying 5-gallon containers of non-RCRA sand into
bucket of backhoe.
9.03
11/20/96
0920
J. Kolb
Dumping sand into roll-off box with backhoe.
9.08
11/20/96
1047
J. Kolb
ERCS emptying containers of sand inside parking bays into bucket
on the backhoe.
9.11
11/20/96
1107
J. Kolb
ERCS placing visqueen, waste samples, and other debris into
RCRA waste roll-off box.
9.15
11/20/96
1250
J. Kolb
View of the secondary staging area with all containers,
visqueen, and debris removed.
9.17
11/20/96
1255
J. Kolb
View of the lean-to and 55-gallon staging areas with all containers
and debris removed. The overpacks are unused empties.
9.20
11/20/96
1433
J. Kolb
Interior of parking bays, overpacks of various waste streams all
the remain on site. ERCS is marking and labeling.
9.21
11/20/96
1505
J. Kolb
View of waste label for Liquid Tars. Class 3. wastestream.
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PHOTOGRAPH IDENTIFICATION SHEET
Camera Serial #: 645489 TDD #: 96-10-0006
Lens Type: 30-70 mm Site Name: Youngstrom Log Homes
Photo No.
Date
Time
By
Description
10.01
11/21/96
0730
J. Kolb
View of waste label for Asbestos, Class 9, wastestream.
10.02
11/21/96
0730
J. Kolb
View of waste label for Sodium hydroxide, Class 8,
wastestream.
10.03
11/21/96
0734
J. Kolb
View of waste label for Potassium peroxide, Class 5.1, waste-
stream.
10.04
11/21/96
0734
J. Kolb
View of waste label for Zinc powder, Class 4.3, wastestream.
10.06
11/21/96
0743
J. Kolb
Close-up view of caulk tube, labeled "Parr Alumilastic, Combus-
tible".
10.08
11/21/96
0802
J. Kolb
ERCS loading overpacks into truck.
10.10
11/21/96
0814
J. Kolb
View of waste label for Waste paint-related material, Class 3,
wastestream.
10.11
11/21/96
0815
J. Kolb
View of waste label for Grease, non-RCRA, wastestream.
10.12
11/21/96
0815
J. Kolb
View of waste label for caulk, non-RCRA, wastestream.
10.13
11/21/96
0815
J. Kolb
View of waste label for hazardous waste, liquid, n.o.s., (oils),
Class 9, wastestream.
10.14
11/21/96
1030
J. Kolb
Interior of truck with all overpacks loaded and secured.
10.15
11/21/96
1054
J. Kolb
View of the interior of the parking bays with all overpacks, debris,
and equipment removed.
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APPENDIX D
POLLUTION REPORTS
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UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
POLLUTION REPORT
I. HEADING
DATE: November 13,1996
FROM: Carl Kitz, EPA OSC, Region 10
DEPT: OEC, EPA-10 (ECL-116)
Telephone 206-553-0125
TO: See Distribution List
SUBJ: Youngstrom Log Homes Removal Action POLREP #1 (Initial Polrep)
Blackfoot, Idaho
II. BACKGROUND
Site ID: SSID# 102T
Action Memo Status: September 26, 1996
Delivery Order Number: 0012-10-040
NPL Status: Non-NPL
State Notification:
Removal Start Date: November 7, 1996
Expected Completion Date: November 22, 1996
Incident Category: Time Critical Removal Action
III. SITE INFORMATION
Incident Category:
The CERCLIS ID for the site is IDD984669192. The SSID for the site is 102T. This is a time critical
removal action.
Site Description:
The Youngstrom Log Homes site is a former sawmill and loghome construction facility that was leased by
Lewis Youngstrom from the Shoshone-Bannock Tribe. Mr. Youngstrom's lease was revoked in 1987 by the
tribe and the property was abandoned. At the request of the tribe, the EPA conducted a removal assessment of
the site in 1992. Site conditions documented at that time indicated that hundreds of 55-gallon drums and
smaller containers were abandoned on site, were exposed to the elements, and were rusty, unlabeled, and in
poor condition. Some appeared to have leaked their contents onto the ground. Samples were collected from
16 of the containers and contaminants detected included volatile organics, semi-volatile organics, pesticides,
and metals. Field screening results indicated the presence of acids, bases, and flammable materials. Eight soil
samples that were also collected targeted areas of stained soil and stressed vegetation. Sample results indicated
contaminants similar to those found in the containers. These results were forwarded to the tribe along with
recommendations concerning clean-up actions. The tribe requested additional assistance from the EPA in June
1996 after it was determined the tribe was unable to fund a clean-up action. At that time the tribe indicated
there are also unconfirmed reports of buried wastes on site.
Physical Location:
The site is located within the Ft. Hall Indian Reservation approximately 3 miles from Blackfoot, Idaho.
The surrounding area is predominantly agricultural in use, with a few scattered homes and businesses located
nearby. The site is bordered on the west and north by an agricultural irrigation canal.
Site Characteristics:
-------
The site consists of approximately 20 buildings in various states of disrepair, numerous piles of soil, wood, and
metal debris, abandoned vehicles, an estimated 500-1,000 containers stockpiled at several on-site locations,
and 2-3 low-lying pits or trenches. The site is fenced with either lograil or barbed wire fence, both of which in
poor condition and are nonexistent in several locations.
IV. RESPONSE INFORMATION
Planned Removal Activities:
All containers will be moved and staged in one convenient location, their contents inventoried, sampled,
and field screened. This data will be used to develop wastestreams for eventual off-site disposal. Soil will be
excavated in areas suspected of waste burial, and soil samples collected. Depending on the analytical results,
soils will also be disposed of off-site along with any buried wastes discovered. To prevent additional waste
dumping or trespassing, a chain-link fence may be installed along the east side of the site, with the tribe to fund
installation of the remainder.
Situation and Next Steps:
Situation: Removal action continues
Personnel On Site: OSC, START-1, ERCS-3
Weather: Skies are partly clear, with light winds and mid-day temperatures in the 50's.
Summary to Date:
Site mobilization occurred on November 7, 1996 with 1 OSC, 5 START, and 2 ERCS. Initial activities
involved preparing the parking bays next to the office building for staging the containers. Due to the suspected
presence of the Hanta Virus, this involved cleaning and sweeping in Level C protection. The area around the
office building was graded for parking and staging of the office trailers, and roads were constructed to the
container stockpiles located at the south end of the site. Once the containers were staged in the parking bays,
START began opening and sampling the contents, and hazard categorized the samples in order to determine
disposal wastestreams. On November 8, 1996 one additional START and ERCS each mobilized to the site.
By November 9, 1996 all the containers were staged and opened, and ERCS began re-staging containers
according to established wastestreams for eventual bulking purposes. A total of 1,145 containers were staged,
opened, and the contents inventoried. Approximately 70 of these were 30-gallon or 55-gallon containers with
material inside (an equal number were empty and were staged separately), and the remainder were 5-gallon
buckets and 1-gallon cans. Sampling of all the containers was completed on November 11, 1996, and hazard
categorization on November 12, 1996. Five START demobilized upon completion of these activities. ERCS
continues to re-stage the containers according to wastestream and expects to begin bulking contents by today.
ERCS also excavated 6 test pits in suspicious locations in search of buried wastes, with the OSC and START
providing oversight. No indication of hazardous wastes were revealed, and most of the material either piled or
buried on site appears to be wood or metal debris. START collected a soil sample from each test pit and will
analyze on site for Pentachlorophenol as a precautionary measure.
Next Steps:
ERCS will continue to bulk contents of the containers according to wastestream and solicit bids for off-site
disposal. Selection of a facility is expected by November 15, 1996. Partial demobilization is also expected for
the same day, with mobilization back to the site for transportation of the wastes off site expected to occur
November 18 or 19, 1996.
V. COST INFORMATION
The costs required to accomplish these actions are summarized below.
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Established
Estimated Costs
Ceilings
Thru Nov. 12. 1996
ERCS
$250,000
$29,371
START
$ 40,000
$22,725
EPA
$ 20,000
$ 4,000
Contingency
$ 27,000
-
Total Project Costs
$337,000
$56,096
VI. DISPOSITION OF WASTES
To date no wastes have been transported off site for disposal.
VII. STATUS
Case pending.
DISTRIBUTION
EPA OEC/Region X, Fax (206) 553-0124
Attention: LeRoy Loiselle, Gary Sink
EPA OEC/Region XIOO, Fax (208) 334-1231
Attention: William Freutel
EPA HQ, Washington D.C., Fax (703) 603-9107
Attention: Terry Eby
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UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
POLLUTION REPORT
I. HEADING
DATE: November 15,1996
FROM: Carl Kitz, EPA OSC, Region 10
DEPT: OEC, EPA-10 (ECL-116)
Telephone 206-553-0125
TO: See Distribution List
SUBJ: Youngstrom Log Homes Removal Action POLREP #2
Blackfoot, Idaho
II. BACKGROUND
Site ID: SSID# 102T
Action Memo Status: September 26, 1996
Delivery Order Number: 0012-10-040
NPL Status: Non-NPL
State Notification:
Removal Start Date: November 7, 1996
Expected Completion Date: November 22, 1996
Incident Category: Time Critical Removal Action
III. SITE INFORMATION
Incident Category:
The CERCLIS ID for the site is IDD984669192. The SSID for the site is 102T. This is a time critical
removal action.
Site Description:
See the initial Polrep (Polrep #1).
Physical Location:
See the initial Polrep (Polrep #1).
Site Characteristics:
See the initial Polrep (Polrep #1).
IV. RESPONSE INFORMATION
Planned Removal Activities:
All containers will be moved and staged in one convenient location, their contents inventoried, sampled,
and field screened. This data will be used to develop wastestreams for eventual off-site disposal. Soil will be
excavated in areas suspected of waste burial, and soil samples collected. Depending on the analytical results,
soils will also be disposed of off-site along with any buried wastes discovered. To prevent additional waste
dumping or trespassing, a chain-link fence may be installed along the east side of the site, with the tribe to fund
installation of the remainder.
-------
Situation and Next Steps:
Situation: Removal action continues
Personnel On Site: OSC, START-1, ERCS-4
Weather: Skies are mostly cloudy, with light to moderate winds and mid-day temperatures in the high 30's.
Snow is forecast for the next several days.
Summary to Date:
Site mobilization occurred on November 7, 1996 with 1 OSC, 5 START, and 2 ERCS. Initial activities
involved preparing the parking bays next to the office building for staging the containers. Due to the suspected
presence of the hantavirus, this involved cleaning and sweeping in Level C protection. The area around the
office building was graded for parking and staging of the office trailers, and roads were constructed to the
container stockpiles located at the south end of the site. Once the containers were staged in the parking bays,
START began opening and sampling the contents, and hazard categorized the samples in order to determine
disposal wastestreams. On November 8, 1996 one additional START and ERCS each mobilized to the site.
By November 9, 1996 all the containers were staged and opened, and ERCS began re-staging containers
according to established wastestreams for eventual bulking purposes. A total of 1,145 containers were staged,
opened, and the contents inventoried. Approximately 70 of these were 30-gallon or 55-gallon containers with
material inside (an equal number were empty and were staged separately), and the remainder were 5-gallon
buckets and 1-gallon cans. Sampling of all the containers was completed on November 11, 1996, and hazard
categorization on November 12, 1996. Five START demobilized upon completion of these activities. ERCS
re-staged the containers according to wastestream in order to facilitate bulking, which began on November 12,
1996. On the same day, ERCS also excavated 6 test pits in suspicious locations in search of buried wastes,
with the OSC and START providing oversight. No indication of hazardous wastes were revealed, and most of
the material either piled or buried on site appears to be wood or metal debris. START collected a soil sample
from each test pit and from other locations, and analyzed the samples on site for pentachlorophenol as a
precautionary measure on November 14, 1996. All 14 of the samples analyzed were non-detect. Today a
fourth ERCS mobilized to the site and the majority of bulking will be completed. In addition, final selection of
disposal facilities is also expected for today.
ERCS will finish bulking the contents of containers on November 18, 1996, with transport of the wastes
off site likely to begin on November 20, 1996. ERCS is still awaiting laboratory analysis of two wastestreams,
with results expected on November 19, 1996. Depending on this data, these wastestreams will either be
recycled or disposed of as hazardous.
Next Steps:
V. COST INFORMATION
The costs required to accomplish these actions are summarized below.
Established
Ceilings
Estimated Costs
Thru Nov. 12. 1996
ERCS
START
EPA
Contingency
$250,000
$ 40,000
$ 20,000
$ 27,000
$41,879
$26,250
$ 4,600
Total Project Costs $337,000
$72,729
-------
VI. DISPOSITION OF WASTES
To date no wastes have been transported off site for disposal.
VII. STATUS
Case pending.
DISTRIBUTION
EPA OEC/Region X, Fax (206) 553-0124
Attention: LeRoy Loiselle, Gary Sink
EPA OEC/Region XIOO, Fax (208) 334-1231
Attention: William Freutel
EPA HQ, Washington D.C., Fax (703) 603-9107
Attention: Terry Eby
-------
UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
POLLUTION REPORT
I. HEADING
DATE: November 19,1996
FROM: Carl Kitz, EPA OSC, Region 10
DEPT: OEC, EPA-10 (ECL-116)
Telephone 206-553-0125
TO: See Distribution List
SUBJ: Youngstrom Log Homes Removal Action POLREP #3
Blackfoot, Idaho
II. BACKGROUND
Site ID: SSID# 102T
Action Memo Status: Signed September 26, 1996
Delivery Order Number: 0012-10-040
NPL Status: Non-NPL
State Notification:
Removal Start Date: November 7, 1996
Expected Completion Date: November 22, 1996
Incident Category: Time Critical Removal Action
III. SITE INFORMATION
Incident Category:
The CERCLIS ID for the site is IDD984669192. The SSID for the site is 102T. This is a time critical
removal action.
Site Description:
See the initial Polrep (Polrep #1).
Physical Location:
See the initial Polrep (Polrep #1).
Site Characteristics:
See the initial Polrep (Polrep #1).
IV. RESPONSE INFORMATION
Planned Removal Activities:
All containers will be moved and staged in one convenient location, their contents inventoried, sampled,
and field screened. This data will be used to develop wastestreams for eventual off-site disposal. Soil will be
excavated in areas suspected of waste burial, and soil samples collected. Depending on the analytical results,
soils will also be disposed of off-site along with any buried wastes discovered. To prevent additional waste
dumping or trespassing, a chain-link fence may be installed along the east side of the site, with the tribe to fund
installation of the remainder.
-------
Situation and Next Steps:
Situation: Removal action continues
Personnel On Site: OSC, START-1, ERCS-3
Weather: Skies are cloudy, with moderate to strong winds and mid-day temperatures in the 50's. Snow and
freezing rain the last several days have made for a muddy site.
Summary to Date:
Site mobilization occurred on November 7, 1996 with 1 OSC, 5 START, and 2 ERCS. Initial activities
involved preparing the parking bays next to the office building for staging the containers. Due to the suspected
presence of the hantavirus, this involved cleaning and sweeping in Level C protection. The area around the
office building was graded for parking and staging of the office trailers, and roads were constructed to the
container stockpiles located at the south end of the site. Once the containers were staged in the parking bays,
START began opening and sampling the contents, and hazard categorized the samples in order to determine
disposal wastestreams. On November 8, 1996 one additional START and ERCS each mobilized to the site.
By November 9, 1996 all the containers were staged and opened, and ERCS began re-staging sampled
containers according to established wastestreams for eventual bulking purposes. A total of 1,145 containers
were staged, opened, and the contents inventoried. Approximately 70 of these were 30-gallon or 55-gallon
containers with material inside (an equal number were empty and were staged separately), and the remainder
were 5-gallon buckets and 1-gallon cans.
Sampling of the containers was completed on November 11, 1996, and hazard categorization on
November 12, 1996. Five START demobilized upon completion of these activities. ERCS continued re-
staging the containers according to wastestream in order to facilitate bulking, which began on November 12,
1996. On the same day, ERCS also excavated 6 test pits in suspicious locations in search of buried wastes,
with the OSC and START providing oversight. No indication of hazardous wastes were revealed, and most of
the material either piled or buried on site appears to be wood or metal debris. START collected a soil sample
from each test pit and from other locations, and analyzed the samples on site for pentachlorophenol as a
precautionary measure on November 14, 1996. All 14 of the samples analyzed were non-detect. On
November 15, 1996 Envirosafe Services, of Idaho Inc., (ESI) of Grandview, Idaho was selected as the disposal
facility. A fourth ERCS mobilized to the site on the same day and bulking and re-staging continued.
On November 18, 1996 one ERCS demobilized from the site, and the majority of bulking was completed.
ERCS re-staged the overpacks in the parking bays in order to get them out of the weather. Today the first roll-
off box was delivered to the site and clean, crushed containers and other non-hazardous waste was placed
inside it. ERCS finished bulking into overpacks and staged these inside the parking bay with the others.
Next Steps:
Two additional roll-off boxes will be delivered to the site on November 20, 1996 and ERCS will bulk
RCRA and non-RCRA debris into them. Labels and markings will also be affixed to these and they will be
transported off site on the same day. The overpacks will also be labeled, and the van truck is scheduled to be
on site November 21, 1996 to transport them to ESI. Demobilization will then occur on November 22, 1996.
V. COST INFORMATION
The costs required to accomplish these actions are summarized below.
-------
Established
Estimated Costs
Ceilings
Thru Nov. 18. 1996
ERCS
$250,000
$44,879 (estimated)
START
$ 40,000
$27,025
EPA
$ 20,000
$ 4,900
Contingency
$ 27,000
-
Total Project Costs
$337,000
$76,804
VI. DISPOSITION OF WASTES
To date no wastes have been transported off site for disposal.
VII. STATUS
Case pending.
DISTRIBUTION
EPA OEC/Region X, Fax (206) 553-0124
Attention: LeRoy Loiselle, Gary Sink
EPA OEC/Region XIOO, Fax (208) 378-5744
Attention: William Freutel
EPA HQ, Washington D.C., Fax (703) 603-9107
Attention: Terry Eby
-------
UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
POLLUTION REPORT
I. HEADING
DATE: November 21,1996
FROM: Carl Kitz, EPA OSC, Region 10
DEPT: OEC, EPA-10 (ECL-116)
Telephone 206-553-0125
TO: See Distribution List
SUBJ: Youngstrom Log Homes Removal Action POLREP #4
Blackfoot, Idaho
II. BACKGROUND
Site ID: SSID# 102T
Action Memo Status: Signed September 26, 1996
Delivery Order Number: 0012-10-040
NPL Status: Non-NPL
State Notification:
Removal Start Date: November 7, 1996
Expected Completion Date: November 22, 1996
Incident Category: Time Critical Removal Action
III. SITE INFORMATION
Incident Category:
The CERCLIS ID for the site is IDD984669192. The SSID for the site is 102T. This is a time critical
removal action.
Site Description:
See the initial Polrep (Polrep #1).
Physical Location:
See the initial Polrep (Polrep #1).
Site Characteristics:
See the initial Polrep (Polrep #1).
IV. RESPONSE INFORMATION
Planned Removal Activities:
All containers will be moved and staged in one convenient location, their contents inventoried, sampled,
and field screened. This data will be used to develop wastestreams for eventual off-site disposal. Soil will be
excavated in areas suspected of waste burial, and soil samples collected. Depending on the analytical results,
soils will also be disposed of off-site along with any buried wastes discovered. To prevent additional waste
dumping or trespassing, a chain-link fence may be installed along the east side of the site, with the tribe to fund
installation of the remainder.
-------
Situation and Next Steps:
Situation: Removal action continues
Personnel On Site: OSC, START-1, ERCS-3
Weather: Skies are partly cloudy, with light winds and mid-day temperatures in the 50's.
Summary to Date:
Site mobilization occurred on November 7, 1996 with 1 OSC, 5 START, and 2 ERCS. Initial activities
involved preparing the parking bays next to the office building for staging the containers. Due to the suspected
presence of the hantavirus, this involved cleaning and sweeping in Level C protection. The area around the
office building was graded for parking and staging of the office trailers, and roads were constructed to the
container stockpiles located at the south end of the site. Once the containers were staged in the parking bays,
START began opening and sampling the contents, and hazard categorized the samples in order to determine
disposal wastestreams. On November 8, 1996 one additional START and ERCS each mobilized to the site.
By November 9, 1996 all the containers were staged and opened, and ERCS began re-staging sampled
containers according to established wastestreams for eventual bulking purposes. A total of 1,145 containers
were staged, opened, and the contents inventoried. Approximately 70 of these were 30-gallon or 55-gallon
containers with material inside (an equal number were empty and were staged separately), and the remainder
were 5-gallon buckets and 1-gallon cans.
Sampling of the containers was completed on November 11, 1996, and hazard categorization on
November 12, 1996. Five START demobilized upon completion of these activities. ERCS continued re-
staging the containers according to wastestream in order to facilitate bulking, which began on November 12,
1996. On the same day, ERCS also excavated 6 test pits in suspicious locations in search of buried wastes,
with the OSC and START providing oversight. No indication of hazardous wastes were revealed, and most of
the material either piled or buried on site appears to be wood or metal debris. START collected a soil sample
from each test pit and from other locations, and analyzed the samples on site for pentachlorophenol as a
precautionary measure on November 14, 1996. All 14 of the samples analyzed were non-detect. Based on this
information, the OSC decided not to pursue further soil extent-of-contamination activities unless additional
information could be found to more accurately determine any areas of waste burial or dumping. On November
15, 1996 Envirosafe Services, of Idaho Inc., (ESI) of Grandview, Idaho was selected as the disposal facility. A
fourth ERCS mobilized to the site on the same day and bulking and re-staging continued.
On November 18, 1996 one ERCS demobilized from the site, and the majority of bulking was completed.
ERCS re-staged the overpacks in the parking bays in order to get them out of the weather. On November 19,
1996 the first roll-off box was delivered to the site and clean, crushed containers and other non-hazardous
waste was placed inside it. ERCS also finished bulking into overpacks and staged these inside the parking bay
with the others.
Two 40-yard dump trucks arrived at the site on November 20, 1996 and ERCS proceeded to empty the 5-
gallon buckets of silica into one of them designated for non-RCRA waste. The empty buckets were crushed
and also placed into the truck. The second truck was used for RCRA waste, including 5-gallon buckets of
varnishes, resins, and adhesives, PPE, the samples hazcatted by the START, visqueen used to bulk and stage
containers on, and crushed, dirty drums. The non-RCRA truck was nearly x/i full, while the RCRA truck was
filled. Both trucks departed around midday. Also on November 20, 1996, ERCS and START began marking
and labeling the overpacks in preparation for transport off site.
Today the tractor trailer truck arrived on site and ERCS began loading the overpacks into it while START
continued with marking and labeling. With the manifests signed this truck was also off site by midday, and a
partial demobilization began, with the return of the remaining heavy equipment and rental item such as the fax
machine and PortaJohns.
-------
Next Steps:
Demobilization will be completed by November 22, 1996, when power and phone service will be shut-
off, and the office trailers retrieved. The OSC, START, and ERCS will depart for home on the same day. The
OSC has decided not to pursue construction of a chain-link fence.
V. COST INFORMATION
The costs required to accomplish these actions are summarized below.
Established
Estimated Costs
Ceilings
Thru Nov. 20. 1996
ERCS
$250,000
$92,453
START
$ 40,000
$28,650
EPA
$ 20,000
$ 5,500
Contingency
$ 27,000
-
Total Project Costs
$337,000
$126,603
VI. DISPOSITION OF WASTES
November 20, 1996:
- ~ 20 cubic yards of non-RCRA debris
- ~ 40 cubic yards of RCRA debris
November 21, 1996:
- (19) 55-gallon overpacks of liquid tars
- (5) 85-gallon overpacks of liquid tars
- (10) 55-gallon overpacks of oil/water mixtures
- (2) 55-gallon overpacks of grease
- (2) 85-gallon overpacks of grease
- (1) 55-gallon overpack of lithium grease
- (45) 55-gallon overpacks of waste paint-related materials
- (1) 55-gallon overpack of asbestos-containing material
- (1) 55-gallon overpack of a caustic solid
- (2) 55-gallon overpacks of lab-packed zinc powder
- (4) 5-gallon lab-packs of oxygen-generating containers
VII. STATUS
Case pending.
DISTRIBUTION
EPA OEC/Region X, Fax (206) 553-0124
Attention: LeRoy Loiselle, Gary Sink
EPA OEC/Region XIOO, Fax (208) 378-5744
Attention: William Freutel
EPA HQ, Washington D.C., Fax (703) 603-9107
Attention: Terry Eby
-------
UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
POLLUTION REPORT
I. HEADING
DATE: January 22,1997
FROM: Carl Kitz, EPA OSC, Region 10
DEPT: OEC, EPA-10 (ECL-116)
Telephone 206-553-0125
TO: See Distribution List
SUBJ: Youngstrom Log Homes Removal Action POLREP #5 (Final Polrep)
Blackfoot, Idaho
II. BACKGROUND
Site ID: SSID# 102T
Action Memo Status: Signed September 26, 1996
Delivery Order Number: 0012-10-040
NPL Status: Non-NPL
State Notification:
Removal Start Date: November 7, 1996
Expected Completion Date: November 22, 1996
Incident Category: Time Critical Removal Action
III. SITE INFORMATION
Incident Category:
The CERCLIS ID for the site is IDD984669192. The SSID for the site is 102T. This is a time critical
removal action.
Site Description:
See the initial Polrep (Polrep #1).
Physical Location:
See the initial Polrep (Polrep #1).
Site Characteristics:
See the initial Polrep (Polrep #1).
IV. RESPONSE INFORMATION
Planned Removal Activities:
All containers will be moved and staged in one convenient location, their contents inventoried, sampled,
and field screened. This data will be used to develop wastestreams for eventual off-site disposal. Soil will be
excavated in areas suspected of waste burial, and soil samples collected. Depending on the analytical results,
soils will also be disposed of off-site along with any buried wastes discovered. To prevent additional waste
dumping or trespassing, a chain-link fence may be installed along the east side of the site, with the tribe to fund
installation of the remainder.
-------
Situation and Next Steps:
Situation: Removal action concluded
Personnel On Site: Not applicable
Weather: Not applicable
Summary to Date:
Site mobilization occurred on November 7, 1996 with 1 OSC, 5 START, and 2 ERCS. Initial activities
involved preparing the parking bays next to the office building for staging the containers. Due to the suspected
presence of the hantavirus, this involved cleaning and sweeping in Level C protection. The area around the
office building was graded for parking and staging of the office trailers, and roads were constructed to the
container stockpiles located at the south end of the site. Once the containers were staged in the parking bays,
START began opening and sampling the contents, and hazard categorized the samples in order to determine
disposal wastestreams. On November 8, 1996 one additional START and ERCS each mobilized to the site.
By November 9, 1996 all the containers were staged and opened, and ERCS began re-staging sampled
containers according to established wastestreams for eventual bulking purposes. A total of 1,145 containers
were staged, opened, and the contents inventoried. Approximately 70 of these were 30-gallon or 55-gallon
containers with material inside (an equal number were empty and were staged separately), and the remainder
were 5-gallon buckets and 1-gallon cans.
Sampling of the containers was completed on November 11, 1996, and hazard categorization on
November 12, 1996. Five START demobilized upon completion of these activities. ERCS continued re-
staging the containers according to wastestream in order to facilitate bulking, which began on November 12,
1996. On the same day, ERCS also excavated 6 test pits in suspicious locations in search of buried wastes,
with the OSC and START providing oversight. No indication of hazardous wastes were revealed, and most of
the material either piled or buried on site appears to be wood or metal debris. START collected a soil sample
from each test pit and from other locations, and analyzed the samples on site for pentachlorophenol as a
precautionary measure on November 14, 1996. All 14 of the samples analyzed were non-detect. Based on this
information, the OSC decided not to pursue further soil extent-of-contamination activities unless additional
information could be found to more accurately determine any areas of waste burial or dumping. On November
15, 1996 Envirosafe Services, of Idaho Inc., (ESI) of Grandview, Idaho was selected as the disposal facility. A
fourth ERCS mobilized to the site on the same day and bulking and re-staging continued.
On November 18, 1996 one ERCS demobilized from the site, and the majority of bulking was completed.
ERCS re-staged the overpacks in the parking bays in order to get them out of the weather. On November 19,
1996 the first roll-off box was delivered to the site and clean, crushed containers and other non-hazardous
waste was placed inside it. ERCS also finished bulking into overpacks and staged these inside the parking bay
with the others.
Two 40-yard dump trucks arrived at the site on November 20, 1996 and ERCS proceeded to empty the 5-
gallon buckets of silica into one of them designated for non-RCRA waste. The empty buckets were crushed
and also placed into the truck. The second truck was used for RCRA waste, including 5-gallon buckets of
varnishes, resins, and adhesives, PPE, the samples hazcatted by the START, visqueen used to bulk and stage
containers on, and crushed, dirty drums. The non-RCRA truck was nearly x/i full, while the RCRA truck was
filled. Both trucks departed around midday. Also on November 20, 1996, ERCS and START began marking
and labeling the overpacks in preparation for transport off site.
On November 21,1996 a tractor trailer truck arrived on site and ERCS began loading the overpacks into
it while START continued with marking and labeling. Once the manifests were signed this truck was off site by
midday, and the OSC, START, and ERCS began demobilizing. This demobilization was completed on
November 22, 1996 when the office trailers, heavy equipment, and rental items were removed from the site,
and power and phone services were shut off. The OSC, START, and ERCS departed for home on the same
day, after the OSC decided not to pursue construction of a chain-link fence.
-------
Next Steps:
The OSC and START are currently producing a removal report summarizing activities, costs, and waste
disposition. The ERCS will assist with information on final costs and waste disposal.
V. COST INFORMATION
The costs required to accomplish these actions are summarized below.
Established Estimated Costs
Ceilings Thru Jan. 22. 1997
ERCS $250,000 $106,233
START $ 40,000 $ 33,850
EPA $ 20,000 $ 5,500
Contingency $ 27,000
Total Project Costs $337,000 $145,583
VI. DISPOSITION OF WASTES
Envirosafe Services of Idaho, Inc.
Grandview, Idaho
Sodium Hydroxide, Solid, (1) 55-gallon drum, 200 pounds
Hazardous Waste, Liquid, n.o.s. (Oil), D008, (10) 55-gallon drums, 550 gallons
RQ, Asbestos, (1) 55-gallon drum, 500 pounds
Non-regulated Grease, (3) 55-gallon drums and (2) 85-gallon overpacks, 200 gallons
RQ Waste Environmentally Hazardous Substances, Solid, n.o.s. (D008), 35 cubic yards
Non-regulated sand, 22,000 pounds
Aptus Rollins OPC
Aragonite, Utah
Waste paint-related materials, D001, D007, D008, F002, F003, (2) 55-gallon drums, 300 pounds
Waste paint-related materials, D001, D006, D007, D008, F002, F003, (43) 55-gallon drums,
13,500 pounds
Tars, Liquid, D001, (19) 55-gallon drums and (5) 85-gallon overpacks, 8,400 pounds
Potassium peroxide, D003, D005, (4) 5-gallon lab-packs, 6 pounds
VII. STATUS
A final removal report documenting all site activities is currently being produced.
DISTRIBUTION
EPA OEC/Region X, Fax (206) 553-0124
Attention: LeRoy Loiselle, Gary Sink
EPA OEC/Region XIOO, Fax (208) 378-5744
Attention: William Freutel
EPA HQ, Washington D.C., Fax (703) 603-9107
Attention: Terry Eby
-------
APPENDIX E
CONTAINER INVENTORY
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
CONTAINER INVENTORY
NOVEMBER, 1996
Container #
Size
Condition
1
5-gallons
dented
2
5-gallons
good
3
5-gallons
good
4
5-gallons
good
5
5-gallons
good, bit rusty
6
5-gallons
good, bit rusty
7
5-gallons
dented and rusty
8
5-gallons
good
9
5-gallons
rusty
10
5-gallons
good
11
5-gallons
rusty
12
5-gallons
rusty
13
1-gallon
rusty
14
5-gallons
rusty with holes
15
5-gallons
rusty
16
5-gallons
rusty with holes
17
5-gallons
dented and rusty
18
5-gallons
good
19
5-gallons
good
20
5-gallons
rusty and open
21
5-gallons
good
22
5-gallons
good
23
5-gallons
good
24
5-gallons
rusty and open
25
5-gallons
rusty
26
1-quart
empty
27
1-gallon
rusty
28
5-gallons
rusty and open
29
5-gallons
dented
30
5-gallons
good
31
5-gallons
good
32
5-gallons
good
33
5-gallons
good
34
5-gallons
good
35
5-gallons
good
36
5-gallons
good
37
5-gallons
good
38
5-gallons
good
39
5-gallons
good
40
5-gallons
dented
41
5-gallons
dented
42
5-gallons
good
43
5-gallons
good
44
5-gallons
good
45
5-gallons
good
46
5-gallons
good
47
5-gallons
rusty
48
5-gallons
dented
Page 1
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
CONTAINER INVENTORY
NOVEMBER, 1996
Container #
Size
Condition
49
5-gallons
dented
50
5-gallons
dented
51
5-gallons
rusty
52
5-gallons
rusty
53
5-gallons
rusty
54
5-gallons
rusty and open
55
5-gallons
rusty and open
56
5-gallons
rusty
57
5-gallons
dented and rusty
58
5-gallons
rusty and open
59
5-gallons
rusty and open
60
5-gallons
rusty and open
61
5-gallons
rusty and open
62
5-gallons
rusty and open
63
5-gallons
rusty and open
64
5-gallons
rusty and open
65
5-gallons
rusty
66
5-gallons
rusty and open
67
5-gallons
rusty and open
68
5-gallons
rusty and open
69
5-gallons
rusty
70
5-gallons
rusty
71
5-gallons
good, open
72
5-gallons
good
73
5-gallons
good
74
5-gallons
rusty
75
5-gallons
good
76
5-gallons
good
77
5-gallons
dented
78
5-gallons
rusty
79
5-gallons
rusty and open
80
5-gallons
rusty
81
5-gallons
rusty
82
5-gallons
good
83
5-gallons
good and open
84
5-gallons
rusty and open
85
5-gallons
rusty and open
86
5-gallons
good
87
5-gallons
good
88
5-gallons
good and open
89
5-gallons
good
90
5-gallons
good
91
5-gallons
dented and open
92
5-gallons
dented
93
5-gallons
dented and open
94
5-gallons
good
95
5-gallons
open
96
5-gallons
good
Page 2
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
CONTAINER INVENTORY
NOVEMBER, 1996
Container #
Size
Condition
97
5-gallons
rusty
98
5-gallons
rusty
99
5-gallons
rusty
100
5-gallons
rusty and open
101
5-gallons
rusty
102
5-gallons
good
103
5-gallons
rusty and open
104
5-gallons
rusty
105
5-gallons
good
106
1-quart
rusty and open
107
1-gallon
rusty and open
108
1-gallon
rusty and open
109
5-gallons
rusty
110
5-gallons
rusty and open
111
5-gallons
rusty
112
5-gallons
rusty
113
5-gallons
rusty
114
5-gallons
rusty
115
5-gallons
rusty
116
5-gallons
rusty
117
5-gallons
rusty
118
5-gallons
good
119
5-gallons
good
120
5-gallons
good
121
5-gallons
rusty
122
5-gallons
rusty and open
123
5-gallons
crushed
124
5-gallons
crushed
125
5-gallons
crushed
126
5-gallons
rusty
127
5-gallons
rusty and open
128
5-gallons
rusty
129
5-gallons
dented
130
5-gallons
good
131
5-gallons
good
132
5-gallons
dented, spilled
133
5-gallons
rusty
134
5-gallons
rusty
135
5-gallons
136
5-gallons
rusty and open
137
5-gallons
good
138
5-gallons
rusty, holes
139
5-gallons
rusty and open
140
5-gallons
rusty
141
5-gallons
rusty
142
5-gallons
rusty
143
5-gallons
rusty
144
5-gallons
white poly, open
Page 3
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
CONTAINER INVENTORY
NOVEMBER, 1996
Container #
Size
Condition
145
5-gallons
black poly, open
146
5-gallons
rusty and open
147
5-gallons
rusty and open
148
5-gallons
rusty and open
149
5-gallons
dented and rusty
150
5-gallons
good
151
5-gallons
rusty
152
5-gallons
dented
153
5-gallons
rusty
154
5-gallons
rusty
155
5-gallons
dented and rusty
156
5-gallons
rusty
157
5-gallons
rusty
158
5-gallons
rusty
159
5-gallons
rusty
160
5-gallons
dented and rusty
161
5-gallons
dented and rusty
162
5-gallons
dented and rusty, open
163
5-gallons
dented
164
5-gallons
rusty
165
5-gallons
rusty
166
5-gallons
rusty
167
5-gallons
dented and rusty
168
5-gallons
rusty
169
5-gallons
rusty
170
5-gallons
rusty
171
5-gallons
rusty
172
1-gallon
rusty
173
1-gallon
rusty
174
5-gallon
rusty and open
175
5-gallon
rusty
176
5-gallon
rusty
177
5-gallon
good and rusty
178
5-gallon
good
179
5-gallon
good and open
180
5-gallon
good and open
181
5-gallon
rusty
182
5-gallon
rusty
183
5-gallon
rusty
184
5-gallon
rusty
185
5-gallon
rusty
186
5-gallon
rusty and open
187
5-gallon
rusty and open
188
5-gallon
rusty and open
189
5-gallon
rusty
190
5-gallon
rusty
191
5-gallon
rusty
192
5-gallon
rusty
Page 4
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
CONTAINER INVENTORY
NOVEMBER, 1996
Container #
Size
Condition
193
5-gallon
rusty and open
194
5-gallon
rusty and open
195
5-gallon
good and rusty
196
5-gallon
good and rusty
197
5-gallon
dented and rusty
198
5-gallon
good and rusty
199
5-gallon
dented and rusty
200
5-gallon
rusty
201
5-gallon
good
202
5-gallon
rusty and open
203
5-gallon
rusty
204
5-gallon
rusty
205
5-gallon
rusty
206
5-gallon
rusty
207
5-gallon
rusty
208
5-gallon
rusty
209
5-gallon
rusty
210
5-gallon
rusty
211
5-gallon
rusty
212
5-gallon
rusty
213
5-gallon
rusty
214
5-gallon
rusty
215
5-gallon
rusty and open
216
5-gallon
rusty
217
5-gallon
good
218
5-gallon
good
219
5-gallon
good
220
5-gallon
good
221
5-gallon
good
222
5-gallon
good
223
5-gallon
rusty and open
224
5-gallon
rusty
225
5-gallon
rusty
226
5-gallon
rusty
227
5-gallon
rusty
228
5-gallon
rusty
229
5-gallon
rusty
230
5-gallon
good
231
5-gallon
rusty
232
5-gallon
rusty
233
5-gallon
rusty
234
5-gallon
good and rusty
235
5-gallon
good and rusty
236
5-gallon
good and rusty
237
5-gallon
good and rusty
238
5-gallon
good and rusty
239
5-gallon
good and rusty
240
5-gallon
rusty
Page 5
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
CONTAINER INVENTORY
NOVEMBER, 1996
Container #
Size
Condition
241
5-gallon
rusty
242
5-gallon
rusty and open
243
5-gallon
rusty
244
5-gallon
rusty
245
5-gallon
good and rusty
246
5-gallon
good and rusty
247
5-gallon
good and rusty
248
5-gallon
good and rusty
249
5-gallon
good and rusty
250
5-gallon
good and rusty
251
5-gallon
good and rusty
252
5-gallon
good and rusty
253
5-gallon
good and rusty
254
5-gallon
good and rusty
255
5-gallon
good and rusty
256
5-gallon
good and rusty
257
5-gallon
good and rusty
258
5-gallon
good and rusty
259
5-gallon
good and rusty
260
5-gallon
good and rusty
261
5-gallon
good and rusty
262
5-gallon
good and rusty
263
5-gallon
good and rusty
264
5-gallon
good and rusty
265
5-gallon
good and rusty
266
5-gallon
good and rusty
267
5-gallon
good and rusty
268
5-gallon
good and rusty
269
5-gallon
good and rusty
270
5-gallon
good and rusty, open
271
5-gallon
rusty and open
272
5-gallon
rusty and open
273
5-gallon
rusty
274
5-gallon
rusty and open
275
5-gallon
good and rusty
276
5-gallon
good and rusty
277
5-gallon
good and rusty
278
5-gallon
good and rusty
279
5-gallon
good and rusty
280
5-gallon
good and rusty
281
5-gallon
good and rusty
282
5-gallon
good and rusty
283
5-gallon
open
284
5-gallon
good
285
5-gallon
good
286
5-gallon
rusty and open
287
5-gallon
good and rusty
288
5-gallon
good and rusty
Page 6
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
CONTAINER INVENTORY
NOVEMBER, 1996
Container #
Size
Condition
289
5-gallon
good and rusty
290
5-gallon
good and rusty
291
5-gallon
good and rusty
292
5-gallon
good and rusty
293
5-gallon
good and rusty
294
5-gallon
rusty
295
5-gallon
dented and rusty
296
5-gallon
rusty
297
5-gallon
dented and rusty
298
5-gallon
rusty
299
5-gallon
rusty
300
5-gallon
rusty
301
5-gallon
rusty
302
5-gallon
good
303
5-gallon
good and rusty
304
5-gallon
dented and rusty
305
5-gallon
rusty
306
5-gallon
dented and rusty
307
5-gallon
good and rusty
308
5-gallon
good and rusty
309
5-gallon
good and rusty
310
5-gallon
rusty and open
311
5-gallon
good
312
5-gallon
rusty
313
5-gallon
rusty
314
5-gallon
rusty
315
5-gallon
good
316
5-gallon
rusty
317
5-gallon
rusty
318
5-gallon
rusty
319
5-gallon
rusty
320
5-gallon
rusty
321
5-gallon
good
322
5-gallon
good
323
5-gallon
good
324
5-gallon
good
325
5-gallon
good
326
5-gallon
good
327
5-gallon
good
328
5-gallon
good
329
5-gallon
good
330
5-gallon
good
331
5-gallon
good
332
5-gallon
dented
333
5-gallon
dented
334
5-gallon
good
335
5-gallon
good
336
5-gallon
good
Page 7
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
CONTAINER INVENTORY
NOVEMBER, 1996
Container #
Size
Condition
337
5-gallon
good
338
5-gallon
good
339
5-gallon
good
340
5-gallon
good
341
5-gallon
good with spillage
342
5-gallon
good
343
5-gallon
good
344
5-gallon
good
345
5-gallon
good
346
5-gallon
good
347
5-gallon
good with spillage
348
5-gallon
good with spillage
349
5-gallon
good
350
5-gallon
rusty and hole
351
5-gallon
rusty
352
5-gallon
rusty
353
5-gallon
rusty
354
5-gallon
rusty
355
5-gallon
rusty
356
5-gallon
rusty
357
5-gallon
rusty
358
5-gallon
rusty
359
5-gallon
rusty
360
5-gallon
rusty
361
5-gallon
good with spillage
362
5-gallon
good with spillage
363
5-gallon
good with spillage
364
5-gallon
good
365
5-gallon
good
366
5-gallon
good
367
5-gallon
dented and rusty
368
5-gallon
rusty and holes
369
5-gallon
rusty and holes
370
5-gallon
rusty
371
5-gallon
rusty
372
5-gallon
rusty and holes
373
5-gallon
rusty and holes
374
5-gallon
dented and rusty
375
5-gallon
rusty
376
5-gallon
rusty
377
5-gallon
rusty and open
378
5-gallon
rusty and open
379
5-gallon
rusty
380
5-gallon
rusty and open
381
5-gallon
rusty and open
382
5-gallon
rusty
383
5-gallon
rusty
384
5-gallon
rusty
Page 8
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
CONTAINER INVENTORY
NOVEMBER, 1996
Container #
Size
Condition
385
5-gallon
rusty and open
386
5-gallon
dented and rusty
387
5-gallon
rusty
388
5-gallon
rusty
389
5-gallon
rusty and open
390
5-gallon
rusty
391
5-gallon
rusty
392
5-gallon
rusty
393
5-gallon
rusty
394
5-gallon
rusty
395
5-gallon
rusty
396
5-gallon
rusty
397
5-gallon
rusty
398
5-gallon
rusty
399
5-gallon
rusty
400
5-gallon
rusty and holes
401
5-gallon
open
402
5-gallon
rusty
403
5-gallon
rusty
404
5-gallon
rusty and open
405
5-gallon
rusty and open
406
5-gallon
rusty
407
5-gallon
rusty
408
5-gallon
dented and rusty
409
5-gallon
good and rusty
410
5-gallon
good and rusty
411
5-gallon
good and rusty
412
5-gallon
good and rusty
413
5-gallon
good and rusty
414
5-gallon
good and rusty
415
5-gallon
good and rusty
416
5-gallon
good and rusty
417
5-gallon
good and rusty
418
5-gallon
good and rusty
419
5-gallon
good and rusty
420
5-gallon
rusty and open
421
5-gallon
good and rusty
422
5-gallon
good and rusty
423
5-gallon
good and rusty
424
5-gallon
good and rusty
425
5-gallon
good and rusty
426
5-gallon
good and rusty
427
5-gallon
good and rusty
428
5-gallon
good and rusty
429
5-gallon
good and rusty
430
5-gallon
good and rusty
431
5-gallon
good and rusty
432
5-gallon
good and rusty
Page 9
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
CONTAINER INVENTORY
NOVEMBER, 1996
Container #
Size
Condition
433
5-gallon
rusty and open
434
5-gallon
dented and rusty
435
5-gallon
dented and rusty
436
5-gallon
rusty
437
5-gallon
rusty
438
5-gallon
dented and rusty
439
5-gallon
dented and rusty
440
5-gallon
dented and rusty
441
5-gallon
dented and rusty
442
5-gallon
dented and rusty
443
5-gallon
rusty and open
444
5-gallon
rusty
445
5-gallon
good
446
5-gallon
open and holes
447
5-gallon
dented and rusty
448
5-gallon
good and rusty
449
5-gallon
good
450
5-gallon
dented
451
5-gallon
rusty
452
5-gallon
rusty
453
5-gallon
rusty
454
5-gallon
rusty
455
5-gallon
dented and rusty
456
5-gallon
dented and rusty
457
5-gallon
rusty
458
5-gallon
dented and rusty
459
5-gallon
rusty
460
5-gallon
rusty
461
5-gallon
rusty
462
5-gallon
good and rusty
463
5-gallon
good and rusty
464
5-gallon
good and rusty
465
5-gallon
good and rusty
466
5-gallon
good and rusty
467
5-gallon
good and rusty
468
5-gallon
good and rusty
469
5-gallon
good and rusty
470
5-gallon
good and rusty
471
5-gallon
good and rusty
472
5-gallon
good and rusty
473
5-gallon
good and rusty
474
5-gallon
good and rusty
475
5-gallon
dented
476
5-gallon
rusty
477
5-gallon
rusty
478
5-gallon
rusty
479
5-gallon
rusty
480
5-gallon
rusty and open
Page 10
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
CONTAINER INVENTORY
NOVEMBER, 1996
Container #
Size
Condition
481
5-gallon
rusty
482
5-gallon
rusty and open
483
5-gallon
rusty
484
5-gallon
good
485
5-gallon
good
486
5-gallon
good
487
5-gallon
good
488
5-gallon
rusty
489
5-gallon
rusty and open
490
5-gallon
rusty
491
5-gallon
rusty and open
492
5-gallon
rusty and open
493
5-gallon
rusty and open
494
5-gallon
rusty and open
495
5-gallon
rusty and open
496
5-gallon
rusty and open
497
5-gallon
rusty and open
498
5-gallon
broken white poly
499
5-gallon
black poly
500
5-gallon
white poly
501
5-gallon
rusty
502
5-gallon
rusty
503
5-gallon
rusty and open
504
5-gallon
rusty
505
5-gallon
rusty and open, holes
506
5-gallon
rusty
507
5-gallon
rusty
508
5-gallon
open white poly
509
5-gallon
rusty
510
5-gallon
rusty
511
5-gallon
rusty
512
5-gallon
rusty and open
513
5-gallon
rusty
514
5-gallon
rusty
515
5-gallon
rusty
516
5-gallon
rusty and open
517
5-gallon
rusty
518
5-gallon
rusty
519
5-gallon
rusty
520
5-gallon
rusty and open
521
5-gallon
rusty
522
5-gallon
rusty and open
523
5-gallon
rusty
524
5-gallon
rusty
525
5-gallon
rusty and open
526
5-gallon
rusty
527
5-gallon
rusty
528
5-gallon
rusty
Page 11
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
CONTAINER INVENTORY
NOVEMBER, 1996
Container #
Size
Condition
529
5-gallon
rusty and open
530
5-gallon
crushed
531
5-gallon
open
532
5-gallon
open
533
5-gallon
rusty
534
5-gallon
rusty
535
5-gallon
dented and open
536
5-gallon
dented and rusty
537
5-gallon
rusty
538
5-gallon
rusty and open
539
5-gallon
dented and rusty
540
5-gallon
dented
541
5-gallon
good and greasy
542
5-gallon
good and greasy
543
5-gallon
good and greasy
544
5-gallon
good and greasy
545
5-gallon
good and greasy
546
5-gallon
good and greasy
547
5-gallon
good and greasy
548
5-gallon
good and greasy
549
5-gallon
good and greasy
550
5-gallon
good and greasy
551
5-gallon
good and greasy
552
5-gallon
good and greasy
553
5-gallon
good and greasy
554
5-gallon
good and greasy
555
5-gallon
good and greasy
556
5-gallon
good and greasy
557
5-gallon
good and greasy
558
5-gallon
good and greasy
559
5-gallon
good and greasy
560
5-gallon
good and greasy
561
5-gallon
good and greasy
562
5-gallon
good and greasy
563
5-gallon
good and greasy
564
5-gallon
good and greasy
565
5-gallon
good and greasy
566
5-gallon
good and greasy
567
5-gallon
good
568
5-gallon
dented
569
5-gallon
dented
570
5-gallon
dented
571
5-gallon
dented
572
5-gallon
rusty
573
1-gallon
dented rusty paint can
574
1-gallon
dented rusty paint can
575
1-gallon
dented rusty paint can
576
1-gallon
dented rusty paint can
Page 12
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
CONTAINER INVENTORY
NOVEMBER, 1996
Container #
Size
Condition
577
1-gallon
dented rusty paint can
578
1-gallon
dented rusty paint can
579
1-gallon
dented rusty paint can
580
1-gallon
dented rusty paint can
581
1-gallon
dented rusty paint can
582
1-gallon
dented rusty paint can
583
1-gallon
dented rusty paint can
584
1-gallon
dented rusty paint can
585
1-gallon
dented rusty paint can
586
1-gallon
dented rusty paint can
587
1-gallon
dented rusty paint can
588
1-gallon
dented rusty paint can
589
1-gallon
dented rusty paint can
590
1-gallon
dented rusty paint can
591
1-gallon
dented rusty paint can
592
1-gallon
dented rusty paint can
593
1-gallon
dented rusty paint can
594
1-gallon
dented rusty paint can
595
1-gallon
dented rusty paint can
596
1-gallon
dented rusty paint can
597
1-gallon
dented rusty paint can
598
1-gallon
dented rusty paint can
599
1-gallon
dented rusty paint can
600
1-quart
dented and rusty
601
1-quart
dented and rusty
602
1-quart
dented and rusty
603
1-quart
dented and rusty
604
1-quart
dented and rusty
605
1-quart
dented and rusty
606
1-quart
dented and rusty
607
1-quart
dented and rusty
608
1-quart
dented and rusty
609
1-quart
dented and rusty
610
1-quart
dented and rusty
611
1-quart
dented and rusty
612
1-quart
dented and rusty
613
1-quart
dented and rusty
614
1-quart
dented and rusty
615
1-quart
dented and rusty
616
1-quart
dented and rusty
617
1-quart
dented and rusty
618
1-quart
dented and rusty
619
1-quart
dented and rusty
620
1-quart
dented and rusty
621
1-quart
dented and rusty
622
1-quart
dented and rusty
623
1-quart
dented and rusty
624
1-quart
dented and rusty
Page 13
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
CONTAINER INVENTORY
NOVEMBER, 1996
Container #
Size
Condition
625
1-quart
dented and rusty
626
1-quart
dented and rusty
627
1-quart
dented and rusty
628
1-quart
dented and rusty
629
1-quart
dented and rusty
630
1-quart
dented and rusty
631
1-quart
dented and rusty
632
1-quart
dented and rusty
633
1-quart
dented and rusty
634
1-quart
dented and rusty
635
1-quart
dented and rusty
636
1-quart
dented and rusty
637
1-quart
dented and rusty
638
1-quart
dented and rusty
639
1-quart
dented and rusty
640
1-quart
dented and rusty
641
1-quart
dented and rusty
642
1-quart
dented and rusty
643
1-quart
dented and rusty
644
1-quart
dented and rusty
645
1-quart
dented and rusty
646
1-quart
dented and rusty
647
1-quart
dented and rusty
648
1-quart
dented and rusty
649
1-quart
dented and rusty
650
1-quart
dented and rusty
651
1-quart
dented and rusty
652
1-quart
dented and rusty
653
1-quart
dented and rusty
654
1-quart
dented and rusty
655
1-quart
dented and rusty
656
1-quart
dented and rusty
657
1-quart
dented and rusty
658
1-quart
dented and rusty
659
1-quart
dented and rusty
660
1-quart
dented and rusty
661
1-quart
dented and rusty
662
1-quart
dented and rusty
663
1-quart
dented and rusty
664
1-quart
dented and rusty
665
1-quart
dented and rusty
666
1-quart
dented and rusty
667
1-quart
dented and rusty
668
1-quart
dented and rusty
669
1-quart
dented and rusty
670
1-quart
dented and rusty
671
1 -pint
rusty soup can
672
1-quart
rusty with spillage
Page 14
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
CONTAINER INVENTORY
NOVEMBER, 1996
Container #
Size
Condition
673
1 -pint
rusty soup can
674
1 -pint
rusty soup can
675
5-gallon
open, rusty, square can
676
5-gallon
dented and rusty
677
5-gallon
dented and rusty
678
5-gallon
good
679
5-gallon
good
680
5-gallon
dented and rusty, hole
681
5-gallon
square, rusty and holes
682
5-gallon
dented and rusty, holes
683
5-gallon
dented and rusty, holes
684
5-gallon
dented and rusty, holes
685
5-gallon
dented and rusty, holes
686
5-gallon
dented and rusty, holes
687
5-gallon
dented and rusty, holes
688
5-gallon
dented and rusty, holes
689
5-gallon
dented and rusty, holes
690
8-gallon
good and open
691
5-gallon
dented and rusty, holes
692
5-gallon
dented and open
693
5-gallon
rusty
694
5-gallon
dented and rusty
695
5-gallon
rusty
696
5-gallon
dented and rusty
697
5-gallon
rusty and holes
698
5-gallon
good
699
5-gallon
square, dented, rusty, and open
700
5-gallon
dented and rusty
701
5-gallon
dented and rusty
702
5-gallon
good
703
5-gallon
dented and rusty
704
5-gallon
good and rusty
705
5-gallon
good and rusty
706
5-gallon
good and rusty
707
5-gallon
good
708
5-gallon
dented and rusty
709
5-gallon
dented and open
710
5-gallon
rusty
711
5-gallon
dented and holes
712
5-gallon
flattened
713
5-gallon
open
714
5-gallon
dented and rusty
715
5-gallon
dented and rusty
716
5-gallon
dented and rusty
717
5-gallon
square, dented and rusty
718
5-gallon
rusty and holes
719
5-gallon
open
720
5-gallon
good, hole in lid
Page 15
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
CONTAINER INVENTORY
NOVEMBER, 1996
Container #
Size
Condition
721
5-gallon
good and open
722
5-gallon
good and open
723
5-gallon
crushed
724
5-gallon
dented and open
725
5-gallon
good
726
5-gallon
rusty and holes
727
5-gallon
rusty and holes
728
5-gallon
dented and rusty
729
5-gallon
rusty and holes
730
5-gallon
rusty and open
731
5-gallon
holes
732
5-gallon
open
733
5-gallon
rusty
734
5-gallon
rusty and holes
735
5-gallon
dented and good
736
5-gallon
rusty and open
737
5-gallon
good
738
5-gallon
holes
739
5-gallon
740
5-gallon
good
741
5-gallon
dented and rusty
742
5-gallon
holes
743
5-gallon
rusty and open
744
5-gallon
dented and rusty
745
5-gallon
746
5-gallon
747
5-gallon
holes
748
5-gallon
crushed
749
5-gallon
good
750
1-gallon
dented rusty paint cans
751
1-gallon
dented rusty paint cans
752
1-gallon
dented rusty paint cans
753
1-gallon
dented rusty paint cans
754
1-gallon
dented rusty paint cans
755
1-gallon
dented rusty paint cans
756
1-gallon
dented rusty paint cans
757
1-gallon
dented rusty paint cans
758
1-gallon
dented rusty paint cans
759
1-gallon
dented rusty paint cans
760
1-gallon
dented rusty paint cans
761
1-gallon
dented rusty paint cans
762
1-gallon
dented rusty paint cans
763
1-gallon
dented rusty paint cans
764
1-gallon
dented rusty paint cans
765
1-gallon
dented rusty paint cans
766
1-gallon
dented rusty paint cans
767
1-gallon
dented rusty paint cans
768
1-gallon
dented rusty paint cans
Page 16
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
CONTAINER INVENTORY
NOVEMBER, 1996
Container #
Size
Condition
769
1-gallon
dented rusty paint cans
770
1-gallon
dented rusty paint cans
771
1-gallon
dented rusty paint cans
772
1-gallon
dented rusty paint cans
773
1-gallon
dented rusty paint cans
774
1-gallon
dented rusty paint cans
775
1-gallon
dented rusty paint cans
776
1-gallon
dented rusty paint cans
777
1-gallon
dented rusty paint cans
778
1-gallon
dented rusty paint cans
779
1-gallon
dented rusty paint cans
780
1-gallon
dented rusty paint cans
781
1-gallon
dented rusty paint cans
782
1-gallon
dented rusty paint cans
783
1-quart
dented rusty paint cans
784
1-quart
dented rusty paint cans
785
1-quart
dented rusty paint cans
786
1-gallon
dented rusty paint cans
787
1-gallon
dented rusty paint cans
788
1-gallon
dented rusty paint cans
789
1-gallon
dented rusty paint cans
790
1-gallon
dented rusty paint cans
791
1-gallon
dented rusty paint cans
792
1-gallon
dented rusty paint cans
793
1-gallon
dented rusty paint cans
794
1-gallon
dented rusty paint cans
795
1-gallon
dented rusty paint cans
796
1-gallon
dented rusty paint cans
797
1-gallon
dented rusty paint cans
798
1-gallon
dented rusty paint cans
799
1-gallon
dented rusty paint cans
800
1-gallon
dented rusty paint cans
801
1-gallon
dented rusty paint cans
802
1-gallon
dented rusty paint cans
803
1-gallon
dented rusty paint cans
804
1-gallon
dented rusty paint cans
805
1-gallon
dented rusty paint cans
806
1-quart
dented rusty paint cans
807
1-gallon
dented rusty paint cans
808
1-gallon
dented rusty paint cans
809
1-gallon
dented rusty paint cans
810
1-gallon
dented rusty paint cans
811
1-gallon
dented rusty paint cans
812
1-gallon
dented rusty paint cans
813
1-gallon
dented rusty paint cans
814
1-quart
dented rusty paint cans
815
1-quart
dented rusty paint cans
816
1-quart
dented rusty paint cans
Page 17
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
CONTAINER INVENTORY
NOVEMBER, 1996
Container #
Size
Condition
817
1-quart
dented rusty paint cans
818
1-quart
dented rusty paint cans
819
1-quart
dented rusty paint cans
820
1-quart
dented rusty paint cans
821
1-gallon
dented rusty paint cans
822
1-gallon
dented rusty paint cans
823
1-gallon
dented rusty paint cans
824
1-gallon
dented rusty paint cans
825
1-gallon
dented rusty paint cans
826
1-gallon
dented rusty paint cans
827
1-gallon
dented rusty paint cans
828
1-gallon
dented rusty paint cans
829
1-gallon
dented rusty paint cans
830
1-gallon
dented rusty paint cans
831
1-gallon
dented rusty paint cans
832
1-gallon
dented rusty paint cans
833
1-gallon
dented rusty paint cans
834
1-gallon
dented rusty paint cans
835
1-gallon
dented rusty paint cans
836
1-gallon
dented rusty paint cans
837
1-gallon
dented rusty paint cans
838
1-gallon
dented rusty paint cans
839
1-gallon
dented rusty paint cans
840
1-gallon
dented rusty paint cans
841
1-gallon
dented rusty paint cans
842
1-gallon
dented rusty paint cans
843
1-gallon
dented rusty paint cans
844
1-gallon
dented rusty paint cans
845
1-gallon
dented rusty paint cans
846
1-gallon
dented rusty paint cans
847
1-gallon
dented rusty paint cans
848
1-gallon
dented rusty paint cans
849
1-gallon
dented rusty paint cans
850
1-gallon
dented rusty paint cans
851
1-gallon
dented rusty paint cans
852
1-gallon
dented rusty paint cans
853
1-gallon
dented rusty paint cans
854
1-gallon
dented rusty paint cans
855
1-gallon
dented rusty paint cans
856
1-gallon
dented rusty paint cans
857
1-gallon
dented rusty paint cans
858
1-gallon
dented rusty paint cans
859
1-gallon
dented rusty paint cans
860
1-gallon
dented rusty paint cans
861
1-gallon
dented rusty paint cans
862
1-gallon
dented rusty paint cans
863
1-gallon
dented rusty paint cans
864
1-gallon
dented rusty paint cans
Page 18
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
CONTAINER INVENTORY
NOVEMBER, 1996
Container #
Size
Condition
865
1-gallon
dented rusty paint cans
866
1-gallon
dented rusty paint cans
867
1-gallon
dented rusty paint cans
868
1-gallon
dented rusty paint cans
869
1-gallon
dented rusty paint cans
870
1-gallon
dented rusty paint cans
871
1-gallon
dented rusty paint cans
872
1-gallon
dented rusty paint cans
873
1-gallon
dented rusty paint cans
874
1-gallon
dented rusty paint cans
875
1-gallon
dented rusty paint cans
876
1-gallon
dented rusty paint cans
877
1-gallon
dented rusty paint cans
878
1-gallon
dented rusty paint cans
879
1-gallon
dented rusty paint cans
880
1-gallon
dented rusty paint cans
881
1-gallon
dented rusty paint cans
882
1-gallon
dented rusty paint cans
883
1-gallon
dented rusty paint cans
884
1-gallon
dented rusty paint cans
885
1-gallon
dented rusty paint cans
886
1-gallon
dented rusty paint cans
887
1-gallon
dented rusty paint cans
888
1-gallon
dented rusty paint cans
889
1-gallon
dented rusty paint cans
890
1-gallon
dented rusty paint cans
891
1-gallon
dented rusty paint cans
892
1-gallon
dented rusty paint cans
893
1-gallon
dented rusty paint cans
894
1-gallon
dented rusty paint cans
895
1-gallon
dented rusty paint cans
896
1-gallon
dented rusty paint cans
897
1-gallon
dented rusty paint cans
898
1-gallon
dented rusty paint cans
899
1-gallon
dented rusty paint cans
900
1-gallon
dented rusty paint cans
901
1-gallon
dented rusty paint cans
902
1-gallon
dented rusty paint cans
903
1-gallon
dented rusty paint cans
904
1-gallon
dented rusty paint cans
905
1-gallon
dented rusty paint cans
906
1-gallon
dented rusty paint cans
907
1-gallon
dented rusty paint cans
908
1-gallon
dented rusty paint cans
909
1-gallon
dented rusty paint cans
910
1-gallon
dented rusty paint cans
911
1-gallon
dented rusty paint cans
912
1-gallon
dented rusty paint cans
Page 19
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
CONTAINER INVENTORY
NOVEMBER, 1996
Container #
Size
Condition
913
1-gallon
dented rusty paint cans
914
1-gallon
dented rusty paint cans
915
1-gallon
dented rusty paint cans
916
1-gallon
dented rusty paint cans
917
1-gallon
dented rusty paint cans
918
1-gallon
dented rusty paint cans
919
1-gallon
dented rusty paint cans
920
1-gallon
dented rusty paint cans
921
1-gallon
dented rusty paint cans
922
1-gallon
dented rusty paint cans
923
1-gallon
dented rusty paint cans
924
1-gallon
dented rusty paint cans
925
1-gallon
dented rusty paint cans
926
1-gallon
dented rusty paint cans
927
1-gallon
dented rusty paint cans
928
1-gallon
dented rusty paint cans
929
1-gallon
dented rusty paint cans
930
1-gallon
dented rusty paint cans
931
1-gallon
dented rusty paint cans
932
1-gallon
dented rusty paint cans
933
1-gallon
dented rusty paint cans
934
1-gallon
dented rusty paint cans
935
1-gallon
dented rusty paint cans
936
1-gallon
dented rusty paint cans
937
1-gallon
dented rusty paint cans
938
1-gallon
dented rusty paint cans
939
1-gallon
dented rusty paint cans
940
1-gallon
dented rusty paint cans
941
1-gallon
dented rusty paint cans
942
55-gallon
dented and rusty, bung
943
55-gallon
dented and rusty, bung
944
55-gallon
dented and rusty, bung
945
30-gallon
bulging with spigot
946
30-gallon
rusty and open
947
55-gallon
rusty, bung
948
30-gallon
rusty, ring
949
55-gallon
dented, bung
950
55-gallon
rusty, bung
951
5-gallon
dented and rusty
952
55-gallon
rusty, ring
953
55-gallon
rusty, bung
954
55-gallon
rusty, bung
955
55-gallon
dented and rusty, bung
956
55-gallon
dented and rusty, bung
957
55-gallon
rusty, bung
958
55-gallon
rusty, bung
959
55-gallon
dented and open
960
55-gallon
good, bung
Page 20
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
CONTAINER INVENTORY
NOVEMBER, 1996
Container #
Size
Condition
961
55-gallon
crushed and open
962
55-gallon
good, bung
963
55-gallon
dented and rusty, bung
964
55-gallon
good, bung
965
55-gallon
good bung
966
55-gallon
good and greasy, bung
967
55-gallon
dented, bung
968
5-gallon
dented
969
55-gallon
bulging, bung
970
1-gallon
rusty paint can
971
55-gallon
good, bung
972
55-gallon
good and greasy, bung
973
55-gallon
dented, bung
974
55-gallon
good, bung
975
55-gallon
good, bung
976
55-gallon
good and greasy, bung
977
55-gallon
rusty and open
978
55-gallon
rusty, bung
979
55-gallon
dented and rusty, bung
980
55-gallon
good and open
981
55-gallon
good and rusty, bung
982
55-gallon
dented and rusty, bung
983
55-gallon
good, bung
984
55-gallon
good, bung
985
55-gallon
rusty, bung
986
55-gallon
rusty and crushed, open
987
55-gallon
rusty and crushed, open
988
55-gallon
good, ring
989
55-gallon
good, ring
990
55-gallon
rusty and open
991
55-gallon
rusty, bung
992
55-gallon
dented and rusty, bung
993
55-gallon
dented and holes, bung
994
55-gallon
dented, bung
995
55-gallon
rusty, bung
996
55-gallon
rusty, bung
997
55-gallon
dented with spillage
998
55-gallon
rusty, bung
999
30-gallon
dented and rusty, bung
1000
55-gallon
dented and rusty, open
1001
55-gallon
dented and rusty, open
1002
55-gallon
dented and rusty, open
1003
55-gallon
good and open
1004
55-gallon
dented and rusty, bung
1005
55-gallon
rusty, bung
1006
30-gallon
rusty with spigot
1007
55-gallon
rusty and open
1008
55-gallon
rusty, bung
Page 21
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
CONTAINER INVENTORY
NOVEMBER, 1996
Container #
Size
Condition
1009
55-gallon
dented, bung
1010
55-gallon
rusty, bung
1011
55-gallon
rusty, bung
1012
55-gallon
rusty, bung
1013
55-gallon
rusty, bung
1014
55-gallon
rusty, bung
1015
55-gallon
dented, bung
1016
55-gallon
dented, bung
1017
55-gallon
rusty and open
1018
55-gallon
dented and open
1019
1-gallon
dented, rusty paint cans
1020
1-gallon
dented, rusty paint cans
1021
1-gallon
dented, rusty paint cans
1022
1-gallon
dented, rusty paint cans
1023
1-gallon
dented, rusty paint cans
1024
1-gallon
dented, rusty paint cans
1025
1-gallon
dented, rusty paint cans
1026
1-gallon
dented, rusty paint cans
1027
1-gallon
dented, rusty paint cans
1028
1-gallon
dented, rusty paint cans
1029
1-gallon
dented, rusty paint cans
1030
1-gallon
dented, rusty paint cans
1031
1-gallon
dented, rusty paint cans
1032
1-gallon
dented, rusty paint cans
1033
1-gallon
dented, rusty paint cans
1034
1-gallon
dented, rusty paint cans
1035
1-gallon
dented, rusty paint cans
1036
1-gallon
dented, rusty paint cans
1037
1-gallon
dented, rusty paint cans
1038
1-gallon
dented, rusty paint cans
1039
1-gallon
dented, rusty paint cans
1040
1-gallon
dented, rusty paint cans
1041
1-gallon
dented, rusty paint cans
1042
1-gallon
dented, rusty paint cans
1043
1-gallon
dented, rusty paint cans
1044
1-gallon
dented, rusty paint cans
1045
1-gallon
dented, rusty paint cans
1046
1-gallon
dented, rusty paint cans
1047
1-gallon
dented, rusty paint cans
1048
1-gallon
dented, rusty paint cans
1049
1-gallon
dented, rusty paint cans
1050
1-gallon
dented, rusty paint cans
1051
1-gallon
dented, rusty paint cans
1052
1-gallon
dented, rusty paint cans
1053
1-gallon
dented, rusty paint cans
1054
1-gallon
dented, rusty paint cans
1055
1-gallon
dented, rusty paint cans
1056
1-gallon
dented, rusty paint cans
Page 22
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
CONTAINER INVENTORY
NOVEMBER, 1996
Container #
Size
Condition
1057
1-gallon
dented, rusty paint cans
1058
1-gallon
dented, rusty paint cans
1059
1-gallon
dented, rusty paint cans
1060
1-gallon
dented, rusty paint cans
1061
1-gallon
dented, rusty paint cans
1062
1-gallon
dented, rusty paint cans
1063
1-gallon
dented, rusty paint cans
1064
1-gallon
dented, rusty paint cans
1065
1-gallon
dented, rusty paint cans
1066
1-gallon
dented, rusty paint cans
1067
1-gallon
dented, rusty paint cans
1068
1-gallon
dented, rusty paint cans
1069
1-gallon
dented, rusty paint cans
1070
1-gallon
dented, rusty paint cans
1071
1-gallon
dented, rusty paint cans
1072
1-gallon
dented, rusty paint cans
1073
1-gallon
dented, rusty paint cans
1074
1-gallon
dented, rusty paint cans
1075
1-gallon
dented, rusty paint cans
1076
1-gallon
dented, rusty paint cans
1077
1-gallon
dented, rusty paint cans
1078
1-gallon
dented, rusty paint cans
1079
1-gallon
dented, rusty paint cans
1080
1-gallon
dented, rusty paint cans
1081
1-quart
dented, rusty paint cans
1082
1-quart
dented, rusty paint cans
1083
1-quart
dented, rusty paint cans
1084
1-quart
dented, rusty paint cans
1085
1-quart
dented, rusty paint cans
1086
1-quart
dented, rusty paint cans
1087
1-quart
dented, rusty paint cans
1088
1-quart
dented, rusty paint cans
1089
1-quart
dented, rusty paint cans
1090
1-quart
dented, rusty paint cans
1091
1-gallon
dented, rusty paint cans
1092
1-gallon
dented, rusty paint cans
1093
1-gallon
dented, rusty paint cans
1094
1-gallon
dented, rusty paint cans
1095
1-gallon
dented, rusty paint cans
1096
1-gallon
dented, rusty paint cans
1097
1-gallon
dented, rusty paint cans
1098
1-gallon
dented, rusty paint cans
1099
1-gallon
dented, rusty paint cans
1100
1-gallon
dented, rusty paint cans
1101
1-gallon
dented, rusty paint cans
1102
1-gallon
dented, rusty paint cans
1103
1-gallon
dented, rusty paint cans
1104
1-gallon
dented, rusty paint cans
Page 23
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
CONTAINER INVENTORY
NOVEMBER, 1996
Container #
Size
Condition
1105
1-gallon
dented, rusty paint cans
1106
1-gallon
dented, rusty paint cans
1107
1-gallon
dented, rusty paint cans
1108
1-gallon
dented, rusty paint cans
1109
1-gallon
dented, rusty paint cans
1110
1-gallon
dented, rusty paint cans
1111
1-gallon
dented, rusty paint cans
1112
1-gallon
dented, rusty paint cans
1113
1-gallon
dented, rusty paint cans
1114
1-gallon
dented, rusty paint cans
1115
1-gallon
dented, rusty paint cans
1116
1-gallon
dented, rusty paint cans
1117
1-gallon
dented, rusty paint cans
1118
1-gallon
dented, rusty paint cans
1119
1-gallon
dented, rusty paint cans
1120
1-gallon
dented, rusty paint cans
1121
1-gallon
dented, rusty paint cans
1122
1-gallon
dented, rusty paint cans
1123
1-gallon
dented, rusty paint cans
1124
1-gallon
dented, rusty paint cans
1125
1-gallon
dented, rusty paint cans
1126
1-gallon
dented, rusty paint cans
1127
1-gallon
dented, rusty paint cans
1128
1-gallon
dented, rusty paint cans
1129
1-gallon
dented, rusty paint cans
1130
1-gallon
dented, rusty paint cans
1131
1-gallon
dented, rusty paint cans
1132
1-gallon
dented, rusty paint cans
1133
1-gallon
dented, rusty paint cans
1134
1-gallon
dented, rusty paint cans
1135
1-gallon
dented, rusty paint cans
1136
1-gallon
dented, rusty paint cans
1137
5-gallon
open
1138
1139
5-gallon
dented and rusty
1140
5-gallon
good
1141
square dented tank
1142
1143
1144
1145
Page 24
-------
APPENDIX F
HAZARD CATEGORIZATION DATA
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
1
Red, paint-like
7
-
7
-
-
-
IS
>200
-
NA
2
Black tar
300
-
-
-
-
-
IS
100-140
-
NA
3
Black tar
400
-
-
-
-
-
IS
100-140
-
NA
4
Dark brown oil
2000
-
5
-
-
-
Floater
100-140
-
NA
5
Hard yellow gel
600
-
7
-
-
-
IS
140-200
-
Organic
6
Hard paint residue
1300
NA
NA
NA
NA
NA
IS
140-200
-
NA
7
Black, crumbly, spongy
5
-
7
-
-
-
Sol ./Cloudy
>200
-
NA
8
Very dry paint
300
-
7
-
-
-
IS
>200
Bluegreen
Organic
9
Black tar
300
-
7
-
-
-
IS/floats
140-200
Green
NA
10
Dry paint
2
-
7
-
-
-
IS
>200
-
NA
11
Rust flakes
600
-
4
-
-
-
IS
Nonflam.
Green
Org. Resd.
12
Dark Motor Oil
2000
-
NA
NA
NA
NA
Sinker
140-200
Green
13
14
Rust flakes
3
-
NA
NA
NA
NA
IS
Nonflam.
Green
NA
15
Oil tar/rusty water
2000
-/+
-/5
-/-
-/-
-/-
/sol.
140-200/
Green/Green
Org./
16
Greenish tar granules
1
-
7
-
-
-
IS
>200
-
Char
17
White granules
2000
-
8
-
-
-
IS
100-140
-
Non-char
18
Clear oil
2000
-
6
-
-
-
Floats
100-140
-
Char
19
Black tar
300
NA
NA
NA
NA
NA
NA
100-140
-
NA
20
Amber gel
0
NA
7
NA
NA
NA
IS/sinks
100-140
-
No soot
21
Brown oil/water
0
-/+
-17
-/-
NA
-/-
Floats/
140-200
-
soot/clean
22
Black tar
>200
NA
NA
NA
NA
NA
NA
100-140
-
NA
23
Black tar
>300
NA
NA
NA
NA
NA
NA
100-140
-
NA
24
Brownish pink sugary powder
0
NA
7
-
NA
-
SS/sinks
-
-
Combust.
25
Red paint sludge and water
10.3
+
7
-
NA
-
IS/sinks
140-200
Bright yellow
Soot
26
Yellow paint flakes
0
NA
7
-
NA
+
IS/sinks
>200
-
No char
27
White granular gel
50
-
7
-
NA
-
SS/emul.
140-200
-
Soot
28
Brownish pink sugary powder
0
NA
7
-
NA
-
SS/sinks
-
-
Combust.
29
Black tar
>300
NA
NA
NA
NA
NA
NA
100-140
-
NA
30
Black tar
>500
-
7
NA
NA
NA
IS
100-140
-
Soot
31
Black tar
1257
NA
7
NA
NA
NA
IS
100-140
-
Soot
32
Black tar
>400
NA
NA
NA
NA
NA
IS
100-140
-
NA
33
Black tar
>200
NA
NA
NA
NA
NA
IS
100-140
-
NA
Page 1
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
34
Black tar
>100
NA
NA
NA
NA
NA
IS
100-140
-
NA
35
Black tar
>300
NA
NA
NA
NA
NA
IS
100-140
-
NA
36
Black tar
>300
NA
NA
NA
NA
NA
IS
100-140
-
NA
37
Black tar
>200
NA
NA
NA
NA
NA
IS
100-140
-
NA
38
Black tar
>300
NA
NA
NA
NA
NA
IS
100-140
-
NA
39
Black tar
>300
NA
NA
NA
NA
NA
IS
100-140
-
NA
40
Black tar
>300
NA
NA
NA
NA
NA
NA
100-140
-
NA
41
Black tar
>300
NA
NA
NA
NA
NA
NA
100-140
-
NA
42
Black tar
>300
NA
NA
NA
NA
NA
NA
100-140
-
NA
43
Black tar
>300
NA
NA
NA
NA
NA
NA
100-140
-
NA
44
Black tar
>300
NA
NA
NA
NA
NA
NA
100-140
-
NA
45
Black tar
>300
NA
NA
NA
NA
NA
NA
100-140
-
NA
46
Black tar
>300
NA
NA
NA
NA
NA
NA
100-140
-
NA
47
Black tar
>300
NA
NA
NA
NA
NA
NA
100-140
-
NA
48
Black tar
>300
NA
NA
NA
NA
NA
NA
100-140
-
NA
49
Black tar
>300
NA
NA
NA
NA
NA
NA
100-140
-
NA
50
Black tar
300
NA
NA
NA
NA
NA
NA
100-140
-
NA
51
Brown sand
0
-
7
-
-
-
IS
>200
-
char
52
Rose-colored sandy powder
0
-
7
-
-
-
IS
Nonflam.
-
char
53
Rose-colored sandy powder
0
NA
NA
NA
NA
NA
NA
>200
-
NA
54
Rose-colored sandy powder
0
NA
NA
NA
NA
NA
NA
>200
-
NA
55
Rose-colored sandy powder
0
NA
NA
NA
NA
NA
NA
>200
-
char
56
Tan sandy powder
0
NA
NA
NA
NA
NA
NA
>200
-
char
57
Rose-colored sandy powder
0
NA
NA
NA
NA
NA
NA
>200
NA
NA
58
Rose-colored sandy powder
0
NA
NA
NA
NA
NA
NA
>200
NA
NA
59
Rose-colored sandy powder
0
NA
NA
NA
NA
NA
NA
>200
NA
NA
60
Rose-colored sandy powder
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
61
Rose-colored sandy powder
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
62
Rose-colored sandy powder
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
63
Tan sandy powder
0
-
7
-
-
-
IS
>200
-
char
64
Rose-colored sandy powder
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
65
Tan sandy powder
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
66
Tan sandy powder
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
67
Tan sandy powder
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
Page 2
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
68
Tan sandy powder
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
69
Rose-colored sandy powder
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
70
Tan sandy powder
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
71
Tan sandy powder
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
72
Black tar
1000
NA
NA
NA
NA
NA
NA
100-140
-
NA
73
Black tar chips
700
NA
NA
NA
NA
NA
NA
140-200
-
char
74
Tan sandy powder
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
75
Black tar
300
NA
NA
NA
NA
NA
NA
140-200
-
NA
76
Tan sandy powder
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
77
Black tar
600
NA
NA
NA
NA
NA
NA
100-140
-
NA
78
Tan sandy powder
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
79
Tan sandy powder
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
80
Light brown sand
1.6
-
7
-
NA
-
SS/sinks
-
NA
inert
81
Light brown sand
1.6
-
7
-
NA
-
SS/sinks
-
NA
inert
82
Gray powder
0
-
7
-
NA
-
SS/susp.
-
NA
-
83
Light brown sand
1.6
-
7
-
NA
-
SS/sinks
-
NA
No soot
84
Light brown sugary powder
1.6
-
7
-
NA
-
SS/sinks
-
NA
inert
85
Light brown sugary powder
1.6
-
7
-
NA
-
SS/sinks
-
NA
inert
86
Chunky milky water
>300
-
7
-
NA
-
IS/sinks
100-140
NA
No soot
87
pinkish/tan sand
1.6
-
7
-
NA
-
SS/sinks
-
NA
No soot
88
Light brown sand
1.6
-
7
-
NA
-
SS/sinks
-
NA
inert
89
Rose-colored sandy powder
1.6
-
7
-
NA
-
SS/sinks
-
NA
inert
90
Thick orange oil
>2000
-
7
-
NA
-
IS/floats
100-140
-
soot
91
Tan sandy powder
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
92
Fine off-white powder
10.5
NA
7
NA
NA
NA
IS/sinks
>200
-
inert
93
Fine off-white powder
10.5
NA
7
NA
NA
NA
IS/sinks
>200
-
inert
94
Black tar
>800
NA
NA
NA
NA
NA
NA
100-140
-
NA
95
Damp tan sand
1.6
-
7
-
NA
-
SS/sinks
-
NA
inert
96
Fine gray powder
0
-
7
-
NA
-
SS/susp.
-
NA
-
97
Fine off-white powder
0
-
7
-
NA
-
SS/susp.
-
NA
-
98
Pink sandy powder
99
Tan sandy powder
1.6
-
7
-
NA
-
SS/sinks
-
NA
inert
100
Damp tan sand
1.6
-
7
-
NA
-
SS/sinks
-
NA
inert
101
Light brown caramel
>150
-
NA
NA
NA
NA
IS
-
-
soot
Page 3
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
102
Amber gel
>2000
NA
7
NA
NA
NA
IS/sinks
100-140
-
No soot
103
Amber gel
25
NA
7
NA
NA
NA
IS/sinks
100-140
-
No soot
104
Damp tan sand
1.6
-
7
-
NA
-
SS/sinks
-
NA
inert
105
Black tar
>400
NA
NA
NA
NA
NA
NA
100-140
-
NA
106
Reddish-brown soil debris
1.5
NA
7
-
NA
-
SS/sinks
-
-
-
107
Amber gel
25
NA
7
NA
NA
NA
IS/sinks
100-140
-
No soot
108
White paint
0
-
NA
NA
NA
NA
IS/sinks
100-140
-
soot
109
Fine off-white powder
10.5
NA
7
NA
NA
NA
IS/sinks
>200
-
inert
110
Damp tan sand
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
111
Damp tan sand
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
112
Rose-colored powder
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
113
Damp tan sand
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
114
Rose-colored powder
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
115
Damp tan sand
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
116
Damp tan sand
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
117
Damp tan sand
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
118
Damp tan sand
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
119
Damp tan sand
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
120
Damp tan sand
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
121
Damp tan sand
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
122
Damp tan sand
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
123
Damp tan sand
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
124
Damp tan sand
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
125
Damp tan sand
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
126
Damp tan sand
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
127
Damp tan sand
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
128
Damp tan sand
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
129
Black tar
100
NA
NA
NA
NA
NA
NA
140-200
NA
NA
130
Black tar
200
NA
NA
NA
NA
NA
NA
100-140
NA
NA
131
Black tar
1000
NA
NA
NA
NA
NA
NA
100-140
NA
NA
132
Black tar
1000
NA
NA
NA
NA
NA
NA
140-200
NA
NA
133
Damp tan sand
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
134
Damp tan sand
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
135
Page 4
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
136
Damp tan sand
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
137
Damp tan sand
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
138
Damp tan sand
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
139
Damp tan sand
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
140
Rose-colored powder
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
141
Damp tan sand
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
142
Rose-colored powder
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
143
Rose-colored powder
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
144
Whitish/brown solid paste
0
NA
9
-
-
-
Soluble
NA
Yellow
Inorg.
145
Tan crystals
0
NA
5
-
NA
NA
SS
140-200
-
char
146
Damp tan sand
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
147
Damp tan sand
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
148
Damp tan sand
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
149
Rose-colored powder
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
150
Light tan sand
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
151
Light tan sand
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
152
Light tan sand
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
153
Light tan sand
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
154
Light tan sand
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
155
Pink sand
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
156
Off-white sand
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
157
Dark brown sand
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
158
Off-white sand
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
159
pink and tan sand
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
160
Pink sand
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
161
Tan sand
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
162
Brown sand
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
163
Pink sand
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
164
Tan sand
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
165
Pink sand
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
166
Brown sand
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
167
Brown sand
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
168
Off-white sand
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
169
Pink sand
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Page 5
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
170
Off-white sand
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
171
Pink sand
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
172
Empty
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
173
Off-white gel
>200
NA
7
-
NA
-
IS/floats
140-200
-
soot
174
175
176
177
178
179
180
181
182
Pink sand
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
183
Brown sand
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
184
185
186
187
188
189
190
Pink Sand
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
191
192
193
194
195
196
197
198
199
200
Off-white sand
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
201
Coffee-colored water
0
+
7
NA
NA
-
Sol.
>200
-
clean
202
203
Page 6
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
204
205
206
207
208
209
210
211
Rose-colored sand/water
0
+/+
7/NA
NA
NA
NA
S/IS
>200
-
No soot
212
Rose-colored sand/water
0
+/+
7/NA
NA
NA
NA
S/IS
>200
-
No soot
213
214
215
Rose-colored sand/water
0
+/+
7/NA
NA
NA
NA
S/IS
>200
-
No soot
216
217
218
219
220
221
222
223
Rose-colored sand
0
+/+
7/NA
NA
NA
NA
S/IS
>200
-
No soot
224
225
226
227
228
229
230
231
232
Off-white sand/water
0
+/+
7/NA
NA
NA
NA
S/IS
>200
-
No soot
233
234
235
236
237
Page 7
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
238
239
240
241
242
243
244
245
246
247
248
249
250
251
252
253
254
255
Off-white sand/water
0
+/+
7/NA
NA
NA
NA
S/IS
>200
-
No soot
256
257
258
259
260
261
262
263
264
265
266
267
268
269
270
271
Page 8
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
272
273
274
275
276
277
278
279
280
281
282
283
284
285
286
287
288
289
290
291
292
293
294
295
296
297
298
299
300
Tan sand
1.1
+
NA
NA
NA
NA
IS
NA
NA
NA
301
302
Milky water/sludge
>900
-/-
7/NA
-/-
NA
-/-
Emul.
<100
-/-
char
303
304
305
Page 9
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
306
Fine gray powder
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
307
308
309
310
311
Fine gray powder
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
312
313
314
315
Black tar
>300
NA
NA
NA
NA
NA
NA
100-140
-
NA
316
317
318
319
320
321
water/off-white sand
0
+
7
NA
NA
NA
NA
NA
NA
NA
322
Clear water/white sludge
>600
-
NA
NA
NA
NA
IS
100-140
-/-
No/char
323
Milky water/white gel
>900
+/+
9/NA
-/-
NA
-/-
Emul.
>200
-/-
No char
324
Black tar
>100
NA
NA
NA
NA
NA
NA
NA
-
NA
325
Clear water/white sludge
>900
-
12
NA
NA
NA
IS
100-140
-/-
No/char
326
Clear water/white sludge
>900
-
12
NA
NA
NA
IS
100-140
-/-
No/char
327
Black tar
>200
NA
NA
NA
NA
NA
NA
100-140
-
NA
328
Black tar
>200
NA
NA
NA
NA
NA
NA
100-140
-
NA
329
Black tar
>200
NA
NA
NA
NA
NA
NA
100-140
-
NA
330
Black tar
>300
NA
NA
NA
NA
NA
NA
100-140
-
NA
331
Gray gravel
0
NA
7
NA
NA
NA
IS
>200
-
No char
332
Black tar
200
NA
NA
NA
NA
NA
NA
100-140
-
NA
333
Black tar
300
NA
NA
NA
NA
NA
NA
100-140
-
NA
334
Black tar
300
NA
NA
NA
NA
NA
NA
100-140
-
NA
335
Black tar
200
NA
NA
NA
NA
NA
NA
100-140
-
NA
336
Black tar
500
NA
NA
NA
NA
NA
NA
100-140
-
NA
337
Black tar
200
NA
NA
NA
NA
NA
NA
100-140
-
NA
338
liquid/sludge
1200
-/-
12
-/-
-/-
-/-
Emul/IS
100-140
-/-
Char
339
Black tar
300
NA
NA
NA
NA
NA
NA
100-140
-
NA
Page 10
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
340
Black tar
100
NA
NA
NA
NA
NA
NA
140-200
-
NA
341
Black tar
200
NA
NA
NA
NA
NA
NA
100-140
-
NA
342
liquid/sludge
1000
-/-
12
-/-
-/-
-/-
Emul/IS
100-140
-
NA
343
344
Black tar
200
NA
NA
NA
NA
NA
NA
100-140
-
NA
345
Black tar
200
NA
NA
NA
NA
NA
NA
100-140
-
NA
346
Black tar
400
NA
NA
NA
NA
NA
NA
100-140
-
NA
347
Black tar
500
NA
NA
NA
NA
NA
NA
100-140
-
NA
348
Black tar
500
NA
NA
NA
NA
NA
NA
100-140
-
NA
349
350
351
352
353
354
355
356
357
358
359
360
361
Black tar
500
NA
NA
NA
NA
NA
NA
100-140
-
NA
362
Black tar
600
NA
NA
NA
NA
NA
NA
100-140
-
NA
363
Black tar
300
NA
NA
NA
NA
NA
NA
100-140
-
NA
364
Black tar
400
NA
NA
NA
NA
NA
NA
100-140
-
NA
365
Black tar
500
NA
NA
NA
NA
NA
NA
100-140
-
NA
366
367
368
369
370
371
372
373
Page 11
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
374
375
376
377
378
379
White chunks
0
-
8
NA
-
NA
IS
Nonflam.
NA
No char
380
381
382
383
384
385
386
387
388
389
390
391
392
393
Tan sand
0
+
8
NA
NA
NA
NA
Nonflam.
-
NA
394
395
396
397
398
399
400
401
402
403
404
405
406
407
Rose-colored sand
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
Page 12
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
408
409
410
411
412
413
414
415
416
417
418
419
420
421
422
423
424
425
426
427
428
429
430
431
432
433
434
435
436
437
438
439
440
441
Page 13
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
442
443
444
445
Black tar
>400
NA
NA
NA
NA
NA
NA
100-140
-
NA
446
Hard black tar
2.4
NA
NA
NA
NA
NA
IS
140-200
-
soot
447
448
449
Black tar
>800
NA
NA
NA
NA
NA
NA
100-140
-
NA
450
Black tar
>300
NA
NA
NA
NA
NA
NA
100-140
-
NA
451
452
Red solid/black tar
0
NA
7
NA
NA
NA
IS/IS
I40-200
+/+
NA
453
454
455
456
457
458
459
460
461
462
463
464
465
466
467
468
469
470
471
472
473
474
475
Page 14
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
476
477
478
479
480
481
482
483
484
485
486
487
488
489
490
491
Tan paste
0
+
7
-
NA
-
Emul.
>200
-
No soot
492
493
494
495
496
Pink paste
0
+
7
-
NA
-
Emul.
>200
-
No soot
497
498
Light gray flakes
0
NA
7
-
NA
-
IS
>200
+
Residue
499
Cloudy water/gel
0
+
7
-
NA
-
Sol./IS
>200
-/-
Clean/soot
500
Gray metallic solid
10
NA
5
-
NA
-
IS
140-200
-
soot
501
Green-purple gel
>2000
NA
NA
NA
NA
NA
IS
140-200
+
Soot
502
Black tar
>300
NA
NA
NA
NA
NA
NA
100-140
-
NA
503
504
White paint
>400
NA
7
NA
NA
NA
IS
140-200
+
soot
505
Solid black tar
0
NA
NA
NA
NA
NA
NA
140-200
-
soot
506
Brownish-red paint
0
NA
7
NA
NA
NA
IS
140-200
-
soot
507
White caulk
>500
NA
7
NA
NA
NA
IS
100-140
+
soot
508
Soil, debris
0
NA
NA
NA
NA
NA
NA
140-200
-
NA
509
Page 15
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
510
511
512
513
514
515
516
517
Brown urethane foam
0
NA
7
NA
-
NA
IS
140-200
-
soot
518
519
520
521
Sticky black tar with solids
0
-
10
-
-
-
Sol.
>200
-
char
522
523
Brown paste
0
+
7
-
NA
-
Sol.
>200
-
char
524
525
526
527
Amber sponge-like crystal
0
-
5
-
-
-
IS
140-200
528
529
530
531
532
533
Brown grease
0
NA
NA
NA
NA
NA
NA
>200
red
NA
534
Brown grease
0
NA
NA
NA
NA
NA
NA
>200
NA
NA
535
536
Brown grease
0
NA
NA
NA
NA
NA
NA
>200
-
NA
537
Grease
0
NA
NA
NA
NA
NA
NA
>200
-
NA
538
539
Pasty brown grease
0
NA
NA
NA
NA
NA
NA
>200
red
NA
540
541
White/yellow liquid
400
+
8
-
-
-
Sol.
Nonflam.
-
residue
542
White/yellow liquid
100
+
8
-
-
-
Sol.
Nonflam.
-
residue
543
Page 16
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
544
545
Yellow oil/tan liquid
200
-/+
7/10
-/-
-/-
-/-
Float/Sol.
>200/Non
-/-
char
546
547
548
549
Brown milky water
>200
+
13
-
-
-
Soluble
>200
-
soot
550
551
552
553
554
555
Brown oil
>200
-
9
-
NA
-
IS
100-140
-
soot
556
557
558
559
560
561
562
563
Brown oil
>200
-
NA
NA
NA
NA
IS
100-140
-
soot
564
565
566
567
Oily water/white gel
>300
-/NA
4
-/NA
NA
-/NA
IS
140-200
-
soot
568
569
Multicolored chunky gel
>600
+
4
-
NA
-
IS
100-140
-
soot
570
Orange goo
1000
-
4
NA
NA
-
Floats
100-140
-
char
571
Brown rubbery chips
500
-
4
NA
NA
-
IS
140-200
-
char
572
Olive brown paint sludge
>300
+
7
-
NA
-
IS
140-200
-
soot
573
Orange paint
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
574
Off-white paint with oil
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
575
White paint with oil on top
NA
NA
NA
NA
NA
NA
NA
100-140
orange
NA
576
Yellow paint
NA
NA
NA
NA
NA
NA
NA
100-140
NA
NA
577
Dark brown oil
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
Page 17
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
578
Red paint
NA
NA
NA
NA
NA
NA
NA
100-140
NA
NA
579
Blue paint with oil on top
NA
NA
NA
NA
NA
NA
NA
100-140
NA
NA
580
Orange paint
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
581
White paint
NA
NA
NA
NA
NA
NA
NA
100-140
NA
NA
582
Dried white paint
NA
NA
NA
NA
NA
NA
NA
>200
-
NA
583
Off-white paint and oil on top
NA
NA
NA
NA
NA
NA
NA
100-140
orange
NA
584
Red wood paint
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
585
Tan paint with oil on top
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
586
Tan paint with oil on top
NA
NA
NA
NA
NA
NA
NA
100-140
NA
NA
587
Tannish-pink paint
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
588
Dried yellow paint
NA
NA
NA
NA
NA
NA
NA
>200
-
NA
589
White paint with oil on top
NA
NA
NA
NA
NA
NA
NA
100-140
NA
NA
590
Gray paint
NA
NA
NA
NA
NA
NA
NA
100-140
NA
NA
591
Orange paint
NA
NA
NA
NA
NA
NA
NA
100-140
NA
NA
592
Dark brown paint
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
593
Pinkish white paint
NA
NA
NA
NA
NA
NA
NA
100-140
orange
NA
594
Blue paint
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
595
Green paint
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
596
Tan paint with oil on top
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
597
Yellow paint
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
598
Yellow paint and oil
NA
NA
NA
NA
NA
NA
NA
140-200
-
NA
599
Green paint
NA
NA
NA
NA
NA
NA
NA
100-140
NA
NA
600
601
602
603
604
605
606
Green paint
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
607
608
609
610
611
Page 18
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
612
613
Greenish-blue paint
NA
NA
NA
NA
NA
NA
NA
>200
-
NA
614
615
616
617
618
619
620
621
622
623
624
625
626
627
628
629
630
631
632
633
634
635
636
637
638
Green paint
NA
NA
NA
NA
NA
NA
NA
140-200
-
NA
639
640
641
642
643
Green paint
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
644
645
Page 19
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
646
647
648
649
650
651
Powdery blue paint
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
652
653
654
655
656
Dry yellow paint
NA
NA
NA
NA
NA
NA
NA
>200
-
NA
657
Blue paint
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
658
659
660
661
662
663
664
Orange paint
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
665
666
667
668
669
670
671
672
673
674
675
676
Amber green crystals
14
-
7
-
-
-
IS
140-200
Slight green
char
677
Clear yellow gel
>20
-
7
NA
NA
NA
IS
140-200
-
soot
678
Gray metallic solid with oil
>1500
NA
7
-
NA
-
IS
140-200
-
soot
679
Solid caramel paint residue
>50
NA
7
-
NA
-
IS
140-200
-
soot
Page 20
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
680
681
682
Brown chunks
0
-
6
-
-
-
IS
140-200
-
char
683
Dry tan chunks
0
-
6
NA
NA
NA
IS
>200
-
char
684
Oily water
0
+
7
NA
NA
NA
NA
>200
-
NA
685
Dry tan chunks
800
-
4
NA
NA
NA
IS
140-200
-
char
686
687
688
Dry tan/silver chunks
0
-
6
NA
NA
NA
IS
>200
-
char
689
690
Amber resin beads
0
-
6
NA
NA
NA
IS
>200
-
char
691
692
693
Red waxy stuff
0
-
6
NA
NA
NA
IS
>200
green
char
694
695
Brown oil/water
0
-/+
NA/7
-
NA
-
IS/sol.
140-200
-
clean
696
697
Amber chunks
1000
-
NA
NA
NA
NA
IS
100-140
-
char
698
Yellow/tan dry paint
2000
-
5
NA
NA
NA
IS
100-140
-
char
699
700
White/tan crumbly chunks
0
-
6
NA
NA
NA
IS
>200
-
char
701
White/tan crumbly chunks
2000
-
6
NA
NA
NA
IS
140-200
-
char
702
Red paint
200
-
10
-
-
-
Soluble
100-140
-
char
703
Silver/amber/green chunks
2000
-
NA
NA
NA
NA
IS
140-200
-
char
704
Oily amber liquid with chunks
1500
-
4
NA
NA
NA
Floats
100-140
NA
NA
705
Oily amber liquid with chunks
300
-
NA
NA
NA
NA
Floats
100-140
NA
char
706
707
Rubbery amber chunks
2000
NA
NA
NA
NA
NA
IS
140-200
NA
char
708
709
White thick paste
100
-
7
NA
NA
NA
IS
140-200
-
NA
710
711
712
713
Green chunks
300
-
NA
NA
NA
NA
IS
>200
green
char
Page 21
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
714
715
Dry brown chunks
100
NA
NA
NA
NA
NA
IS
>200
-
char
716
Pasty white goo
0
-
8
-
NA
-
Soluble
>200
-
char
717
718
Silver/brown chunks
0
-
NA
NA
NA
NA
IS
>200
-
char
719
720
721
722
723
724
725
Red paint
300
-
NA
NA
NA
NA
NA
140-200
-
char
726
727
728
Carmel-colored goo
500
-
NA
NA
NA
NA
Floats
100-140
-
char
729
730
731
Dry white chunks
0
-
NA
NA
NA
NA
IS
>200
-
char
732
Dry green chunks
0
-
NA
NA
NA
NA
IS
>200
-
char
733
Hard amber chunks
200
-
NA
NA
NA
NA
IS
140-200
-
char
734
Hard amber chunks
0
-
NA
NA
NA
NA
IS
>200
-
char
735
Solid black tar
1000
-
NA
NA
NA
NA
IS
100-140
-
char
736
Hard gray paint flakes
0
-
NA
NA
NA
NA
IS
140-200
-
char
737
Hard amber chunks
2000
-
NA
NA
NA
NA
IS
140-200
-
char
738
Light brown crystals
0
NA
7
-
NA
-
IS
>200
-
soot
739
Multi-colored dry paint
>1500
+
&
NA
NA
NA
IS
100-140
-
soot
740
Multi-colored dry paint
>2000
NA
NA
NA
NA
NA
NA
100-140
-
soot
741
gray-green paint sludge
>1500
NA
5
NA
NA
NA
IS
100-140
-
soot
742
743
744
Solid orange goo
0
NA
7
-
NA
-
IS
140-200
-
soot
745
Solid bluegreen chalk
7
NA
NA
NA
NA
NA
NA
100-140
greenblue
clean
746
Amber yellow paint residue
>1400
NA
NA
NA
NA
NA
NA
100-140
-
soot
747
Clear liquid
>300
+
1
-
NA
-
Soluble
100-140
+
clean
Page 22
-------
748
749
750
751
752
753
754
755
756
757
758
759
760
761
762
763
764
765
766
767
768
769
770
771
772
773
774
775
776
777
778
779
780
781
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Rusty water/tar
>40
+/NA
7/NA
NA
NA
NA
Sol./IS
140-200
Multicolored oil and paint sludge
>2000
NA
NA
NA
NA
NA
NA
100-140
Dry white paint
NA
NA
NA
NA
NA
NA
NA
140-200
green
Silver/tan powder
NA
NA
NA
NA
NA
NA
NA
100-140
Silver metallic paint
NA
NA
NA
NA
NA
NA
NA
100-140
Brown sludge
NA
NA
NA
NA
NA
NA
NA
>200
orange
Amber gel
NA
NA
NA
NA
NA
NA
NA
100-140
orange
Dry amber gel
NA
NA
NA
NA
NA
NA
NA
NA
green
Green paint
NA
NA
NA
NA
NA
NA
NA
NA
green
White paint
NA
NA
NA
NA
NA
NA
NA
140-200
Amber gel
NA
NA
NA
NA
NA
NA
NA
100-140
orange
Blue paint
NA
NA
NA
NA
NA
NA
NA
100-140
orange
Solid orange paint
NA
NA
NA
NA
NA
NA
NA
100-140
orange
Tan paste/yellow liquid
NA
NA
NA
NA
NA
NA
NA
100-140
orange
Dried orange paint
NA
NA
NA
NA
NA
NA
NA
100-140
greenblue
Orange and white paint
NA
NA
NA
NA
NA
NA
NA
100-140
orange
White paint
NA
NA
NA
NA
NA
NA
NA
100-140
orange
Dry gray paint
NA
NA
NA
NA
NA
NA
NA
140-200
orange
Brown/yellow liquid
NA
NA
NA
NA
NA
NA
NA
100-140
Gray paint
NA
NA
NA
NA
NA
NA
NA
140-200
Red liquid
NA
NA
NA
NA
NA
NA
NA
140-200
White/amber paint
NA
NA
NA
NA
NA
NA
NA
100-140
orange
Brown/yellow liquid
NA
NA
NA
NA
NA
NA
NA
140-200
Green paint
NA
NA
NA
NA
NA
NA
NA
100-140
Page 23
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
782
Dry gray paint
NA
NA
NA
NA
NA
NA
NA
140-200
orange
NA
783
Green paint
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
784
785
786
787
Orange and white liquid
NA
NA
NA
NA
NA
NA
NA
100-140
orange
NA
788
Green liquid
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
789
790
Dry gray paint
NA
NA
NA
NA
NA
NA
NA
100-140
orange
NA
791
Orange and white liquid
NA
NA
NA
NA
NA
NA
NA
100-140
green
NA
792
Brown/white paint
NA
NA
NA
NA
NA
NA
NA
140-200
orange
NA
793
Brown gel
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
794
Greenish yellow paint
NA
NA
NA
NA
NA
NA
NA
140-200
green-blue
NA
795
Orange liquid
NA
NA
NA
NA
NA
NA
NA
100-140
green
NA
796
Brown gel
NA
NA
NA
NA
NA
NA
NA
100-140
green-orange
NA
797
Grease
NA
NA
NA
NA
NA
NA
NA
100-140
orange
NA
798
Grease
NA
NA
NA
NA
NA
NA
NA
100-140
orange
NA
799
800
Red paint
NA
NA
NA
NA
NA
NA
NA
140-200
-
NA
801
Orange liquid
NA
NA
NA
NA
NA
NA
NA
140-200
-
NA
802
Rust-colored liquid
NA
NA
NA
NA
NA
NA
NA
>200
-
NA
803
White gel
NA
NA
NA
NA
NA
NA
NA
100-140
NA
NA
804
Dry gray paint
NA
NA
NA
NA
NA
NA
NA
140-200
orange
NA
805
806
807
Yellow gel
NA
NA
NA
NA
NA
NA
NA
140-200
-
NA
808
809
810
811
Orange/amber paint
NA
NA
NA
NA
NA
NA
NA
100-140
orange
NA
812
Orange resin
NA
NA
NA
NA
NA
NA
NA
100-140
orange
NA
813
White paste
NA
NA
NA
NA
NA
NA
NA
140-200
-
NA
814
Yellow gel
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
815
Grease
NA
NA
NA
NA
NA
NA
NA
140-200
-
NA
Page 24
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
816
NA
NA
NA
NA
NA
NA
NA
100-140
orange
NA
817
Orange paint
NA
NA
NA
NA
NA
NA
NA
100-140
orange
NA
818
Dry white paint
NA
NA
NA
NA
NA
NA
NA
>200
-
NA
819
Orange paint
NA
NA
NA
NA
NA
NA
NA
100-140
orange
NA
820
Red paint
NA
NA
NA
NA
NA
NA
NA
100-140
orange
NA
821
822
823
824
825
826
827
828
829
830
831
832
833
834
835
836
837
838
839
840
841
842
843
844
845
846
847
848
849
Page 25
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
850
851
Amber gel/Dry gray paint
NA
NA
NA
NA
NA
NA
NA
100-140
orange
NA
852
853
854
855
856
857
858
859
860
861
862
863
864
865
866
867
Dry blue paint
NA
NA
NA
NA
NA
NA
NA
140-200
orange
NA
868
Solid orange paint
NA
NA
NA
NA
NA
NA
NA
140-200
orange
NA
869
870
Tan/amber paint
NA
NA
NA
NA
NA
NA
NA
140-200
orange
NA
871
872
873
874
875
876
877
878
879
White ACM
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
880
White ACM
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
881
White ACM
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
882
White ACM
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
883
White ACM
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Page 26
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
884
White ACM
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
885
White ACM
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
886
White ACM
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
887
White ACM
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
888
White ACM
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
889
White ACM
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
890
White ACM
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
891
White ACM
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
892
White ACM
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
893
White ACM
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
894
White ACM
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
895
Orange resin
NA
NA
NA
NA
NA
NA
NA
100-140
orange
NA
896
White ACM
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
897
Off-white powder
NA
NA
NA
NA
NA
NA
NA
>200
orange
NA
898
Dense gray powder
NA
NA
NA
NA
NA
NA
NA
>200
-
NA
899
Off-white powder
NA
NA
NA
NA
NA
NA
NA
>200
orange
NA
900
901
Off-white powder
NA
NA
NA
NA
NA
NA
NA
>200
orange
NA
902
Solid orange paint
NA
NA
NA
NA
NA
NA
NA
100-140
orange
NA
903
Solid orange paint
NA
NA
NA
NA
NA
NA
NA
100-140
orange
NA
904
Solid gray paint
NA
NA
NA
NA
NA
NA
NA
140-200
green
NA
905
Solid black paint
NA
NA
NA
NA
NA
NA
NA
140-200
-
NA
906
Orange liquid
NA
NA
NA
NA
NA
NA
NA
100-140
orange
NA
907
Black sand
NA
NA
NA
NA
NA
NA
NA
>200
orange
NA
908
Off-white powder
NA
NA
NA
NA
NA
NA
NA
>200
orange
NA
909
Off-white powder
NA
NA
NA
NA
NA
NA
NA
0
orange
NA
910
Thick orange liquid
NA
NA
NA
NA
NA
NA
NA
100-140
orange
NA
911
912
Solid gray paint
NA
NA
NA
NA
NA
NA
NA
140-200
-
NA
913
Beige solid
NA
NA
NA
NA
NA
NA
NA
>200
-
NA
914
Solid black paint
NA
NA
NA
NA
NA
NA
NA
>200
green
NA
915
Solid white paint
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
916
Dry black paint
NA
NA
NA
NA
NA
NA
NA
140-200
orange
NA
917
Orange resin
NA
NA
NA
NA
NA
NA
NA
140-200
orange
NA
Page 27
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
918
Dry red paint
NA
NA
NA
NA
NA
NA
NA
100-140
orange
NA
919
Dry white paint
NA
NA
NA
NA
NA
NA
NA
>200
orange
NA
920
Dry gray paint
NA
NA
NA
NA
NA
NA
NA
140-200
-
NA
921
White ACM
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
922
Dry gray paint
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
923
Orange resin
NA
NA
NA
NA
NA
NA
NA
100-140
orange
NA
924
Black paint
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
925
926
Off-white powder
NA
NA
NA
NA
NA
NA
NA
>200
orange
NA
927
White ACM
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
928
White crystalline salt
0
NA
10
-
NA
-
SS
>200
-
Clean
929
Off-white powder
NA
NA
NA
NA
NA
NA
NA
>200
orange
NA
930
Orange chunky liquid
NA
NA
NA
NA
NA
NA
NA
>200
faint green
NA
931
Dark orange solid with liquid
NA
NA
NA
NA
NA
NA
NA
100-140
blue
NA
932
White ACM
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
933
Yellow gel
NA
NA
NA
NA
NA
NA
NA
140-200
orange
NA
934
935
Solid yellow paint
NA
NA
NA
NA
NA
NA
NA
140-200
blue
NA
936
Brown solid
NA
NA
NA
NA
NA
NA
NA
>200
-
NA
937
Beige caked substance
NA
NA
NA
NA
NA
NA
NA
>200
-
NA
938
Orange resin
NA
NA
NA
NA
NA
NA
NA
100-140
orange
NA
939
Off-white powder
NA
NA
NA
NA
NA
NA
NA
>200
orange
NA
940
Off-white liquid/clear liquid
NA
NA
NA
NA
NA
NA
NA
<100
orange
NA
941
Orange resin
NA
NA
NA
NA
NA
NA
NA
100-140
orange
NA
942
Dirty brown water
0
+
7
NA
NA
-
Soluble
>200
-
clean
943
944
Black sludge
0
+
NA
NA
NA
NA
NA
>200
-
soot
945
946
Dry tan paint chips
0
NA
NA
NA
NA
NA
NA
140-200
green
soot
947
Brown oil/rusty water
>17
-/+
8/6
NA
NA
NA
IS/Sol.
100-140
-/-
soot/clean
948
White crystals with rust
0
-
12
-
-
-
Soluble
>200
-
no soot
949
Dark brown sludge
>50
-
7
NA
NA
NA
IS
140-200
-
soot
950
Black tar
0
NA
NA
NA
NA
NA
NA
140-200
-
soot
951
Brown viscous oil
0
-
NA
NA
NA
NA
NA
>200
-
NA
Page 28
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
952
Brown viscous oil
0
NA
NA
NA
NA
NA
NA
140-200
-
soot
953
Yellow paint/tar
0
NA
NA
NA
NA
NA
NA
>200
-
char
954
955
956
957
958
Brown oil
0
-
7
-
-
-
Floats
>200
-
char
959
Brown oil
0
-
7
-
-
-
Floats
140-200
-
char
960
Brown grease
0
-
NA
NA
NA
NA
NA
140-200
-
char
961
Black tar
600
-
NA
NA
NA
NA
NA
100-140
-
char
962
Yellow liquid
10
-
5
-
-
-
Floats
140-200
-
char
963
964
Amber liquid
0
NA
NA
NA
NA
NA
Floats
140-200
-
char
965
966
Yellow oil/water
0
-/+
-17
NA
NA
NA
Floats/
140-200
-
char
967
Oil/water
0
-/+
6
NA
NA
-/-
Float/Sol.
140-200
-/-
char
968
969
Black tar
250
-
NA
NA
NA
NA
NA
100-140
-
char
970
Rubbery amber chunks
2000
NA
NA
NA
NA
NA
NA
100-140
-
char
971
Black oil
0
NA
NA
NA
NA
NA
NA
140-200
-
char
972
Black tar
600
NA
NA
NA
NA
NA
NA
10-140
-
char
973
Green oil/water
0
-/+
6
NA
NA
NA
Float/Sol.
140-200
-
char
974
975
976
Black tar
150
NA
NA
NA
NA
NA
NA
140-200
-
NA
977
Brown chunks
0
NA
NA
NA
NA
NA
NA
>200
-
char
978
Silver flakes
150
NA
NA
NA
NA
NA
NA
140-200
-
char
979
Tar/oil residue
0
NA
NA
NA
NA
NA
NA
>200
-
char
980
981
Oil/water
0
-/+
NA/7
NA
NA
NA
Floats/Sol.
>200
-
clean
982
983
Black oil/water
0
-/+
NA
NA
NA
NA
NA
>200
-
NA
984
Black oil/water
>40
-/+
NA/7
NA
NA
NA
NA
140-200
-
NA
985
Brown oil/rusty water
0
-/+
NA/7
NA
NA
NA
NA
>200
-
NA
Page 29
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YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
986
Soil/damp paint
0
NA
NA
NA
NA
NA
NA
NA
NA
NA
987
988
Solid black cake
0
NA
8
NA
NA
NA
IS
>200
-
soot
989
Solid black cake
0
NA
8
NA
NA
NA
IS
>200
-
soot
990
Black chunks
0
NA
NA
NA
NA
NA
NA
>200
-
NA
991
992
993
994
Black tar
100
NA
NA
NA
NA
NA
NA
140-200
-
NA
995
996
Brown water
0
+
6
NA
NA
NA
Soluble
Nonflam.
-
residue
997
998
999
Brown rubbery chunks
2000
NA
NA
NA
NA
NA
NA
NA
NA
NA
1000
Black granules
0
-
6
NA
NA
NA
IS
>200
-
char
1001
One big black chunk
500
-
NA
NA
NA
NA
NA
NA
NA
NA
1002
1003
Black liquid
100
+
7
NA
NA
NA
Soluble
Nonflam.
-
char
1004
Silver-colored tar
250
NA
NA
NA
NA
NA
NA
100-140
-
NA
1005
1006
1007
1008
Red jam-like substance
400
-
NA
NA
NA
NA
Floats
100-140
-
NA
1009
Rusty water
0
+
7
NA
NA
NA
Soluble
>200
-
clean
1010
Orange rusty water
>20
+
7
-
NA
-
Soluble
>200
-
clean
1011
1012
Dark brown water
0
+
7
-
NA
-
Soluble
>200
-
NA
1013
Rusty water
0
+
7
NA
NA
NA
Soluble
>200
-
char
1014
1015
Light blue clear liquid
0
+
9
-
NA
+
Soluble
100-140
+
Clean
1016
Light brown oil
0
-
NA
NA
NA
NA
IS
140-200
-
NA
1017
Black tar
0
+
6
NA
NA
NA
NA
>200
-
char
1018
Oil/water
0
-/+
NA/6
NA
NA
NA
NA
140-200
-
char
1019
Page 30
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
1020
1021
1022
1023
1024
1025
Dry gray paint
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
1026
1027
1028
1029
1030
1031
1032
1033
1034
1035
1036
1037
Gray/amber paint
NA
NA
NA
NA
NA
NA
NA
100-140
orange
NA
1038
1039
1040
1041
1042
1043
1044
1045
1046
1047
1048
1049
1050
1051
1052
1053
Gray/amber paint
NA
NA
NA
NA
NA
NA
NA
100-140
orange
NA
Page 31
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YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
1054
1055
1056
1057
1058
1059
1060
1061
1062
1063
White/amber paint
NA
NA
NA
NA
NA
NA
NA
100-140
orange
NA
1064
1065
Black tar
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
1066
Dried white paint
NA
NA
NA
NA
NA
NA
NA
>200
-
NA
1067
Dry gray paint
NA
NA
NA
NA
NA
NA
NA
140-200
-
NA
1068
White paint
NA
NA
NA
NA
NA
NA
NA
100-140
NA
NA
1069
Gray paint flakes
NA
NA
NA
NA
NA
NA
NA
>200
NA
NA
1070
Dark brown oil
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
1071
Amber rubbery resin
NA
NA
NA
NA
NA
NA
NA
140-200
NA
NA
1072
Gray paint
NA
NA
NA
NA
NA
NA
NA
140-200
NA
NA
1073
1074
1075
Dried white paint
NA
NA
NA
NA
NA
NA
NA
140-200
-
NA
1076
Dried white paint
NA
NA
NA
NA
NA
NA
NA
>200
-
NA
1077
Dry red paint
NA
NA
NA
NA
NA
NA
NA
Nonflam.
NA
NA
1078
1079
Brown gel
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
1080
Dark brown oil
NA
NA
NA
NA
NA
NA
NA
140-200
-
NA
1081
1082
Fluorescent red paint
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
1083
1084
1085
1086
1087
Page 32
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YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
1088
1089
1090
1091
Zinc powder
NA
NA
NA
NA
NA
NA
NA
Nonflam.
NA
NA
1092
1093
1094
Black paint
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
1095
Gray paint
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
1096
Bright yellow paint
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
1097
Dry tan powder
NA
NA
NA
NA
NA
NA
NA
>200
-
NA
1098
Oil and gray paint
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
1099
Yellow paint
NA
NA
NA
NA
NA
NA
NA
100-140
NA
NA
1100
Black paint
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
1101
Black paint
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
1102
Black paint
NA
NA
NA
NA
NA
NA
NA
140-200
-
NA
1103
Zinc powder
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
1104
White paint residue
NA
NA
NA
NA
NA
NA
NA
>200
-
NA
1105
Clear yellow liquid
NA
+
12
NA
NA
NA
NA
>200
-
NA
1106
1107
Brown gel
NA
NA
NA
NA
NA
NA
NA
140-200
red
NA
1108
Gray paint
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
1109
Brownish yellow paint
NA
NA
NA
NA
NA
NA
NA
140-200
-
NA
1110
Black tar
NA
NA
NA
NA
NA
NA
NA
140-200
-
NA
1111
1112
Gray paint
NA
NA
NA
NA
NA
NA
NA
140-200
-
NA
1113
Tan paint
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
1114
1115
Gray paint
NA
NA
NA
NA
NA
NA
NA
100-140
NA
NA
1116
Dark brown gel
NA
NA
NA
NA
NA
NA
NA
140-200
-
NA
1117
Hard green paint
NA
NA
NA
NA
NA
NA
NA
140-200
NA
NA
1118
White paint
NA
NA
NA
NA
NA
NA
NA
140-200
NA
NA
1119
Paint oil with no pigment
NA
NA
NA
NA
NA
NA
NA
100-140
NA
NA
1120
Dark brown oil/yellow paint
NA
NA
NA
NA
NA
NA
NA
100-140
-
NA
1121
Page 33
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YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Sample
Number
Description
PID
FID
Watesmo
PH
Sulf.
Cyan.
Oxid.
Water
Sol/React
Flamm.
Bielstien
Char
1122
1123
1124
1125
1126
1127
1128
1129
White crystals
NA
-
8
NA
NA
NA
IS
>200
NA
char
1130
1131
1132
1133
1134
Wood oil
NA
NA
NA
NA
NA
NA
NA
100-140
NA
NA
1135
1136
Varathane varnish
NA
NA
NA
NA
NA
NA
NA
100-140
NA
NA
1137
Brown paint
NA
NA
NA
NA
NA
NA
NA
140-200
-
NA
1138
1139
Oil/water
NA
NA
NA
NA
NA
NA
NA
>200
-
NA
1140
Black tar
NA
NA
NA
NA
NA
NA
NA
>200
NA
NA
1141
1142
Gray chunks
0
-
7
NA
-
-
NA
Nonflam.
-
-
1143
1144
Yellow oily liquid
0
-
NA
NA
NA
NA
Floats
140-200
-
NA
1145
Page 34
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YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
Tin catalyst, silicon rubber
Varnish
Green/red paint
Chared
Dry latex paint
Chlor-n-Oil >500 ppm
Chlor-n-Oil >500 ppm
Same as sample 11
Inorganic, silica
Insoluble in acid
IS in hexane; SS in acid
Some water content
IS in acid, SS in hexane
IS in hexane; SS in acid
No reaction with acid
Page 35
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
No rection with acid
Page 36
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
free water
zinc dust
Page 37
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
IS in acid
Page 38
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
Sodium bicarbonate
Page 39
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
Page 40
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
Page 41
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
Page 42
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
Very ignitable with lots of soot
Page 43
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YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
Zinc dust
Zinc dust
Salt residue
Page 44
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
Page 45
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
Page 46
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
Page 47
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
Chlorinated
Page 48
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
Detergent
Chlorinated paint
Chlorinated paint
Soluble in Hexane
IS in hexane
Chlorinated
Page 49
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YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
IS in hexane
Lithium
Lithium grease
Page 50
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
Oil and water
Absorbent
Soluble in hexane
Soluble in hexane
Soluble in hexane
Soluble in hexane
Page 51
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
Page 52
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
Page 53
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
SS in hexane
IS in hexane and acid
Page 54
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YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
No reaction in acid
No reaction in acid
Page 55
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YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
Absorbent
IS in hexane
IS in hexane and acid
IS in hexane
IS in hexane and acid
alcohol/acid mix?
Page 56
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
Page 57
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
Page 58
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
Page 59
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
Page 60
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
Page 61
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
Asbestos? IS in hexane
Absorbent
Page 62
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
Kerosene?
Oil or kerosene
Kerosene?
Page 63
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
SS in hexane
SS in hexane
Absorbent
Water
Roofing tar
Burns like alcohol
Page 64
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
Page 65
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YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
Page 66
-------
YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
Americoat Label
Lithium
Page 67
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YOUNGSTROM LOG HOMES REMOVAL SITE
BLACKFOOT, IDAHO
HAZARD CATEGORIZATION RESULTS
NOVEMBER, 1996
Other
Reaction with acid; inorganic salt
Kerosene or hydraulic oil
Page 68
-------
APPENDIX G
IMMUNOASSAY TEST KIT INFORMATION
-------
Pentachlorophenol
• Intended Use
Fw detBclton b1 petilicUwoptKIHil in water Igroundwator.
tuHnca wtltr, well wetei). F» (nil. crap. Hid 'food use refer Id
iptcilic application t jllecu.
fw use h SW-846 HnWWI 0 "SciMnim I*
Ptmwhhropheno/l by ImntuwHS#** sea Otfancron Technical
0«btinfrODD04
• Principle
It* PastidilDroph* not RbFIO Anay® epptas tin principles el
erayme tmked enmunosnrbent amy 6U5AI to (he determination
oi pesitadiloropfunsJ The samp* to Ira t»fl*d it tiitii, along
withanawymi conjugate. 1 o 1deposable 1tsi lube, followed by
paramagnetic particles Willi antibothoi specific to
'pen1 BcMoraptarml attached. Both the pentachbrepheiinl (which
may be ml la samp* I width* ann*ne late led peril ecMorophtnol
Itke Biuyme conji-gaftl compete fur snidbady binding silts on the
magnetic piroclrt At Ihe end ef hi incubation pnned •
magnetic field li applied to hold the paramagnetic partidei Mth
pentachlorophenot and labeled pentechfcornptienol anateg hound li
Iht Mtiboitai on the pertide*. in prepertioa to the* original
concomrMiou) in (he lube and allow the unbound raajeMi 10 Ik
ttecnnled Aftir decerning the particles are wuhed with
Washing H ut I Br
The presence of pensachtorapheiwl is detected by Biding!he
e nivm* sobstrale Ihydroyen poronidtl and I he chromagen
0.3..5.5'teitameihyll»enjiitinef. The tMryme-tjiieled
pern BcWottpho not analog boiuid to the penl etsbloropher.:-:
eMiboo* cataHyKts the conwfjMin of Ihe substrate! chramngei
nurture la a co'inred product After an incubation period, the
reaction is impped and stabiied by the addition of »e*d Since
the labeled pentachtorophenol (cmijugalej was « competition with
iht ifilabeled pentacMoropherwl (s-anplel for I he entiodf sites.
Hie ciwor uenuopwJ <» ilnemolr j..b(iCrti.»l»lt~ the
coiicenlranee of penlachlcropnenol in the sample.
• Reagents
1. AnMcMrqpftM1a1 Aaliodr Caifiki Pmamsgmttc Partickt
The pBiilachlornphenol antibody Irabbtc inn pant acHornphenei: is
COVBlently Pound to paramagnetic particles. which are inspected
in buffered sai ne unl h prasarval ive and stafctoers.
30 tail ltd one 20 int. vtal
1 0© test hit: ona 65 ml v«l
2. fewschlaof/ltenai iruinm Cflrjjttjmw
The horwiadish peromdBse WRPl Labels d pe ntachloropheno;
analog is diluted in tbuitered saline with preservative and
nabifceps
30 lest kit one 10 «nL viat
100 test kit oi»35tnLwal
3. Puflttdilaraphttic/ SfamAroSr
T hree concert iai ions [0.1,2,0,100 ppbl of penlachturopbensl
standards«buffeted safire wit h preseivatMr and stsbiliiBTi are
supplied Each'vol contains 2 0 ml
4. Ctmtrd
A toiwaM ration fipproi enatety 1 ppb) of pentacfiloropheiipl in
buffered taliiie evilk preiervcliva siabiSart A JOml
volume is suppied m one vial
5. flfawfiSero JfanrfW
Buflttred sain* conlBirung prasutvsiive and»labilBBrt wittioul
aoy deleitatle pentathlofophenci1
3D tBtl h>1: piw 10 mi vial
100 test lit: one 35 mL wal
S, Colli S c/tHm
A Mtaion of hyiragen perwide anil 3,3',5.5'
iBlnmethp-lbeiifflfine in an organic base
30 last kit one 70«nL met
100ns1kit- une 85 mL nM
?, Stoppmsj Sehtim
A sohitim of sufunc ncsd (0 5%)
34) ibsI bit. one 20 mL ral
1 DO lest hit one 80 mL vial
£ WtshtQg Soffv
BdHerti tali?* containing piesBrvatml and uahilcsn
30ten kit ant 70ml wal
100 Ie it k i m ISOmLwrt
3 Test Tms
Pofytlyrnria tuboi Qfii are packagad in a tot.
30 test kit: one 30 tube boi
1 DO fait h it thnsa 3B tube hoses
• Reagent Storage end Stability
Store ail reagents HI 2 6f°C. Btnotlnci*. Reapents may be
UStd until the expiration date on the box. Th» Itsl tubti/tguir*
m Sfitaot ttatHjH an/Htm antf may be tt&ed unvulslv ttan
ttm rstgsnts ie mww retnpe/atar space.
Cansult st ate. loc bI and fa [IbtbI ngulttiivis lor propa r disposal of
al reagenta.
• Materials Required but Not Provided
In addition to the reagents provided the fallowing dems are
BiientiBlfor Ihe perfornance oil he teat:
Pipet!" Precision pipet s capable of
deiwimfiQ 2110,250 and 508 ul
and a 1 0 ml repeating pipei
Voflej Miier* Ttiermolyw Man M«, Scaetiflc
Industries VorlBi Genie, or
a-quiwahant
Magnetic Separation Rack*
flPAT™ RaPfO AnBin=r" orei?jiuBhnJ
photomBter capabli of raa^ngs
at 450 nro
• These items Bra available liom Ohmtcron.
• Sample Information
This procedure is racommanded for ose with waltr samples
Other snmplei may re gum mcKtific Btiens to the prptadure and
thouM be throughly yaliitatad.
SemplBS containing gross particuldt* matter should i* fifceied
ft.g 0 2 um Anolopru 25 Plus. Whatman, tnc.) It remove
particles.
Samples winch hatve been preserved *nth moaocluwoactlic acid
ur other acids, shouM he neutralijEd witfi at rang base e.g. SN
f4aOH, prior to assay
I f the pfifltachlornpEienol concentration of a samce an reeds 10
ppb, the sample is sublet la repeal testing using a tsati
sample. A ten told or graUM MM of the •n.iple is
rec«nmenrled wilh an apptopiiate Bm«i«1 of Diueni,2ero
Standard or Sum pel tHusnt. F-or tKam pie, in a separata test t ube
make a ten-fold dAition hy eALmg 100 il Of the sample in 900 uL
of Diliwntflaso Standard- Mm thoroughly betere essaymg
Perform Ilia assay oecorrtiryg to the Aiivy Procedure and obi air.
fins results by multiplying the value obtain by lie dilution factor
• g 10.
The presence of the Mlowmgnibstancti up to 250 pgm were
found to ham no signrfleant effect on PentMhloraptafiol RaFID
A nay ra raid caicium, copper, manganese, megneiium. mercury,
nckel. iiilratt, phoiphate. tulfite, (IwiiulfatB and nnc. in
eddrtinn, son ,m chfoMle up l« 0.65 M tulfalt to ID DM ppm
(onto 50 ppm and hianic acid to 10 ppn, showed no ajnifiuanl
aifact en eesuhs,
• Reagent Preparation
AII re egs nit must ba aflnwe d 1 p cchbb ti room itmceratuns anc
tin antibody coupled parBmajnetic panicles should be mixes
thoroughly before ute
• Procedural Notes and Precautions
As with ail anmunonteys. a consistent lechmqui is the key to
opianef performanct To obtaei the greetait precision, be rure it
treat each tuba in an »di!fiticalmanner
-------
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tfttiitiltJ foi ?lfniwf«i el room Iffiffepttiliftf
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»ili ciwife whs ipiiid limli ill fn&Mj
mi itssvid ttwtf l:N P:tshM:IS
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tsiCil'ftfsteMiie I BSD 5
fi^idilefti^driitiaflg SI-SU 5
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%i:lsl@sv a&fc$rt, taMByi teMfiin,, cip-1817-
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ihu -n>n A
!ftl sAtof! al ippiBijimsIg'l^ 1 p-pit &1
#d will ste Pt'SUKWarsflieria^ H-tPlC5 AfiS'i
»iR€fe! ihm ir» inciifc-J ii evfery ran ismI
siP'fpslte^ AttffllMf li
isl«4l If i&cti l«3>drfttarv
« '• "*'i ' •1 ^ »•
I ' ! ¦ 'P \ f >jII1
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Oiteiii'lMa Siwiiaiifl, ¦
Si-s8iifitf 1-,. §. 1 psh
J, I @ pfti
.Sr®iforrf3,. 1'J.G Bill
I i s i( \>{ I "ll 1 si t If, I , SEt „ ^ p."
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III il', >' 'I J II ' 1 h^t' ill «i ([(» ». II Ijtk' ' „h
Mil ill# bOO tel. fyte
nrtB a 1st 1 tc 2 ficofiii®4iii'»w?ii5
cislw# fii? 3-D ftiwytii ®l I1WP' ii«pf'|i#f
BP'-Sififf p Fht Wagwiic Sspsrafieii Iflc* i-c^ two 111
* ; i
I* (MfBStf s®s
Hp %€-¥
1.110
10%
* ; >,-I Ji?•-
S@ wlii'lisWiwi wlii'f ifi i iliiifi' c#f8{|yfJ:t.l cri
tppfififeiSf 1^ IIS #®li.f tsTi.ptef from %ctlioii.l tcrill I
Ailif *tl lliflWli is ft
\u ;f'A Ms'i• ->|| r;-'. i'[ ^ m 1 # i
iwifltl It - Q.980I.
% f;i«'',11' i ^rh t? >a<*: u ,-i
,l '1HV<
I hi Itllawfiig
All Wlti' SllllSfli
Urn
Mfiifiilfiil
% try I wife a$*
sfi iiiiium rrtirunHd!
r .mi up . ij;
f llfitr
i1 i • \ -ii kE
Availaliiliff
Mffrttowptwi®! PfilK«iicf Swptei
t • >i! \ Km., r U f p - F (I.» in
iii! C sled m Kit
CP Sampte liifitiiw til
/y
(1 *i
li
y
KV \ / A J
-------
Pentachlorophenol
Sample Extraction Kit
i OHMICRON
, rtir ffmilltr fHfli'rcm e
» Intended Use
For use n conjunction y.rfh HaPID Prep™ SoS Cofltction Kit and
i he PanlaehioropbanoUtaPlD Assay® Kil (or de ta mnnalion of
peril achlnrap«heriel In soi.
F* use at SW 8*8 Melhod 4010 "Streamm lor
Peril addwophenol t>v Immunoassay" sea Ohmtcion BuAetlrt
itwkim.
• Principle
re n!adilorophei»l is a brood spec"nan pesticide use d m 1 lia wood
and paper irntustry *.s a fungicide to protect agaiiul iurgal ret *nd
it an inseclicide lor llw ror.lrol of taunilti and wood boreig
«ihc1* Prim ary applicat bw in tha industry include pre»*row ion
ot utility poles, railway lei. marine piengs, and fence post) aoc
II a tfcna n ducat in papa r and pulp mttng Paniacidorophenol is
alio uied at a f»rar* herbicide. especially it a pre harwst
def«Uin« in cotton iaiminj It it the most widely used
chlnrc phfi 'ml pa d Icide and it has beta delected at harardou)
waste tilts m I he Unit aif Slitet Peal achiorophe nc residue i
may centamlnaie sod, welts, growuSwnta r and surl ace wat er due
to spifla, drift sndnmolf
Tim defridation ef pa nttddoiophe nal under atmospheric
condition} occon by phatolyui m aqualic systems, ptololysn
ond biodegradBlinn are believed to be the dominant processes In
toil, peMachloiopfaiial fe»odegradti oy becoming t»p«dly
melebolued by acchnaledmicroorganisms. Panlachlornpbenal
da jradirtion occurs most rap vlly m soils of h«gh organic anil
mostture content with itmperadiwn lauxaMt le microbial
aclwity
Tin lui t.ui-1aiiNju hi ukd riai iw nep r B*i«tn.*
• Bf mttff/u using digital ba)mK«:
Option I. Remove tcrew cap Tore lha aoilcollector atlhds
plunge r rod. C ollecl Itw tod "By valine", level it off and push Ihe
sod and plunger | a the but torn of the lube Reattach plunger rod
an.; weigh Ihe tuba containing ihe toil. Subtract erignal weigh!
from final weight la datamin* tod wn-jhi Record the wiight of
the toil.
Oplicn 2. Remove the screw cap and plunger rod from an amply
collection tube. Position lha plonger al ihe boltom ol the
cotaclion tute. Attach the rod base pace provided and place the
lust in art upright punion mlha balance and tare weight Weigh
10 ± 0.1 gram of soit ell d I he lube .Re cord t he soil we ight
3. [mactian. Position the sod collection tut* camaimg a sc-d
sample upright in Ih* slyrolaam rack and add 20 mL ol the
eppropitaie enraclion solution. Screw llw cap Iwiihout filtaii on
Itgh'ly and make Hire lhat Ihe liter cap u secured Shake
vigorously and continuously for at feast 80 second* Additional
shaking may ta required lo break lap large or dry soil aggregates
Foul ion the co>acl«n lube upright in lha rick and allow the
mnture to lit *t Itatt Ihn ninutas. Longer a
-------
t 1" »n p ' hi' Hi » < S 1 k ^ ' [• 1 1i "»» I ( k '[
Hi®!riiniiricimtiff, iit&ck
li* islwipr litil Ed ihe ftep.f of ifw Siisatettm ftapaw *he
lh 1,11 ii„ [ 'I mil I i "V. t"*\ "P. ) liM' f
||, , II ,i f, II, Mi .15 « 11 P'ipii H ¦' PK't f ( lr 1* ' .it »'
t'G mi iNe iiM Mii le tiw if® lilttlf Ifl ifif itwtjfii 5 b* Uim
sii i ik§ iy#r tuM. lfip% tlftti pttiiw» i# ills pssfffjif I?wife.
1 f - i •' aiii" i*"»; » :u tk*h r ,s fi. * . i>1 '» > i >'
§§ffM. Fit it# via* with ippmfBffiiv tin-M
$$§s 0.1 li 1 mil Cinp H* wat. Tbt n fefltawf in
priflfn wwfttfi® wpfetii .itttlytii with B-sPlS t»ip Wis. TNs
%%!< wit up tft I nl ol lit.fiii tlsftf stilt #*smil wittiM *%
SBMtd. 1 he literals gffli isfwf ftoH icMwifslitMl n il tfete wt«t?
$l**r|w Itwg tiltur! ciAciwt wslfortip® 111 #s®l 81 rasfs
iiS 1ft 5-9 E:C|.
* >'! 11i> -'. Ph«« ;»< hit".
Usiftg ih§ ppi provided Irifiife 50 pi nf the ®sirici tatcfiy
trts i fial Pe?iii.s€lilisf@piwiiil iitfttl Btiusfsi GBfftU Ifa liv
ii-« 'is; ii i' 1 x Ji
Thn fwmI'
> SM tUiKsiifi#! sy * simple* accorriir4!
P'tmiacMttriiNi-Ml Jtiiay
iuidtion of Hfl'Suiti
M$fytn@ i
iht MOfjriu
f A ' ¦ ,IV I > \ "J UK (
prawUm. JfyVfsgs nonnrv -tf&d
tuts 10%.. §3 i:8 £3
, ;-h , fU '» \" n/'r» , * i, .'( <( i ^ -, ic
tiltawtSf ktyeix fl #fit iKiditi It fb® %M prt&
ft® tflritl»p pocedos®: 10D pgm oi-oisif, 16H0 pim €C;
!J !»J .(I« S.C ! i) -i» N
«Eastffccti'
Course
»remtr wi%tf ftcsw^if wii be mmmwA tf i«ifae!
Ullfsitel. Ip.priw.ftiilil| f5% if tdtfciS siiilffite?
fiesWfti If il* tw\ fws#te «ifeifetn for 3Q
» if'< L.s^a
cat!! mm I ii Vi !m pen^rnigrofsftH
Hi ift itiii .ipftffl it t ppu ysipf 1^- RaF'iG Pup
*cW«rop^e5oi flsPilJ Ai.iay si ippfpsins
pcittf W'ti
risfeitts,
hp K » 1. 11' I 'I X MSI PflilfI
tUtlpSWUlf IK
20%. This ifpC'
feii?i#pwisas i1
i¥!taciiife$ ml
•«>p ,'lt( '
mUmUi
ii . ^kiin
!VH'| '
«r ir 'iieliitei:i! iftttfaiifst 6W4lCt
OltiiCfui 0*|p^
Sfttei Hips?t®is!
i"A. ^ k \*, i M h k 1
j|0BIS4#-ll|1 * F«S1SIS88!
w
\ \
%
ftaX.
N1'
s<
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Ml b I" I '^hr' -|,N ¦ l E( ' II \*\ II1' i I t?( lK.' 1 I' ¦ t. |iv>v'l V i ¦ •- Il
iilioWft ifeiw, 1 Nt ii-lri-fiit #iit iplii Mrl usiiiitril w^lfc ik
AMPLE fii i Itlll twtpte WilWui I§1 II'WS iWiHi ifl ISSli? D,f*>n ..t, uni r i.i...- ,i , .(l, a h
' ' ^ >• |! t , k "k »" ai!> .) f\\' p t IP •titiii. kf'i »l '; l|fK
1 if 2.1 ifli:
iQ j*p|i « .? 5 ssffi • cuiv£#iiiffllufii d? {tffPl acfes^opN
tewiiisSS^s wBf*
Range of Dit#ctio-n
pliS-LffOllltf i% (IJRli iff- (UTiHinCHl
ii*" - ii ;f 11 ™ «'i' » s rtiv f P"4'
, th8 ft#|p dI fclitlics ift wil n Hill pp# i-§
Nr fifflpiti: wttt pe-rtf «c &Sn ro^tamnf c®tirt.rti«fti|r«iltr llnw
lippw- im retsai sastsi iht itei'l frslrtEi e®i bt fwlter ifihiii
wft itPIB iwi^iiis ihs nifff-iil
fa irttv*.! TIS dteilesi I5S ul ®f Ailt-iJ iisirscl piui llSsni
i » i"> it1, 0 'In \ rA>* ' '' h w- H» f ii l v 1 >»i I 1« '
f lh I' H" s*1 > \ n,h- l' ') t ' lit -M "I »!<>' I tf f||
itew. 1 ta rstp ®f felitli#! I®f ^MseAiijfgii^ntji ii
whiskM it ISi ppffi
; ExMCtiKi Results
# IS* S®np #al;sw fiGlBf iiti Ifci ni Ilw l®&!
ftill dipfii in pit ofi ll* £irt iipsi#| 1te tsisi
if Is si' srimtiien a-titewli oi
pitecii si i in siifl
wnl Inat-i l^ft* wiisif -ws!^
iqiI cB'ftesilrtl-ftiii srf 'I 0S1.1 &*«i I
i su&fecled ia ilw ®fa0vt
* i' M ' I ii ! I >i »>
li f ¦ « -! 'Hi l »M
¦ » * til . ¦¦ t. . „» . «: ,,u-:s ! 1 - k n'»r ¦
" ' "II 1 |V- I ' Ih t 111 # >Hl.
ffwii Oifstcrim
jP^it $fe(&
fiiii Kfi%nipisfia t Swip* A 08! 38
Ertraaum Krt S'D mtjifi)
M'iktill Asist
[ K - « 1
..!!.? M!!!« Ml'" A ¦ i! 1 ¦
-V-,' ...
UE 1150123
1 ^ k' n u i m h , m »'
Pjifi-ftfete Qiiiictf Eilwite ICSD12"
-------
APPENDIX H
UNIFORM WASTE MANIFESTS
-------
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APPENDIX I
IDAHO STATE JOURNAL NEWSPAPER ARTICLE
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I #Y
: . • Journal photo by Kathy Corgalelli
i CIST employee contracted by the Environmental Protection Agency looks into rusted cans at
i former Youngstrom Log Homes site In Fort Hall. ,
r HALL 1—'.The Environ-
? ment|lp|rotection Ageiiey is doing
a detailed cleanup of toxic wastes
J 4t tl^Sformer Youngstrom Log
Home^site on the Fort Hall Indian
Reseiimion, : - , ¦'./ • ;i%-,
• Tttraftte is on State Highway
91, afottt a mile west of the first
BlackMiL e»t off Interstate >16.
The clf&tiiip began last Thursday
and i^fcectod to be completed by
cted EPA workers'have'
lerous containers of such
-tanccs as paint, solvent
_ sealant, said Car! kitz,
EPA Begion 10 official from Seat-
tle,,
Kit&faid all the workers wear
mask^'^hile searching the build-
finds
at site
ings because they are aware of the
1 possibility of contracting han-
tavirus from mouse droppings.
"A hantavirus ease was reported
last summer at the reservation.
The Idaho health department said
the male victim appeared to have
been exposed to mouse droppings
inside and outside an old building.
The cleanup crew discovered
the toxic substances were con-
tained in a variety of containers
ranging from 55-gallon / metal
drums to small rusted paint cans,
.^e EPA refponded to arequeat
, from the Shoshone-Bannock Tribes
¦to clean up the site, Kitz said. The
tribes could not afford the cleanup,
so'the EPA"'is looking'for other
• ways to defray the costs.
. He said the organization plans
to recycle as many of the products
See TOXIC, AT ~
OX1C
21 1
» Continued from A1
1 I,
M possible to recover clean-up costs. Empty
3 runs are being flattened to make trans-
4»rtihg them easier.
5?on-recyclable items will probably be
|iiken to the nearest toxic waste disposal
i: te, Kitz said.
' C?ews also are doing chemical test® to de-
termine what all the substances are, Kitz
said.
He said he did not know if the substances
were left behind when Youngstrom Log
Homes left the site several years ago or if
other people used the deserted buildings to
store waste. -
No one at the tribal office was available
for comment this morning.
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