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COMMERCE BUSINESS DAILY ISSUE OF SEPTEMBER 20,1999 PSA#2435Kaiser Hill Company, LLC, Building 850, P.O. Box 464, Golden, Colorado
80402 C -- SOURCES OF SOIL REMEDIATION TECHNOLOGIES SOUGHT SOL KH900660 DUE
101599 POC Steve Heiman, (303) 966-7922 E-MAIL: Click here to contact
the Subcontract Administrator, steve.heiman@rfets.gov. Kaiser-Hill
Company, L.L.C.(Contractor), is the Integrating Management Contractor
at the U.S. Department of Energy's (DOE), Rocky Flats Environmental
Technology Site, Golden, Colorado (RFETS). The Contractor is currently
planning the environmental remediation of the 903 Pad Area at RFETS.
RFETS is located approximately 16 miles northwest of Denver, Colorado.
The 903 Pad Area is comprised of the following three areas which are
adjacent to each other: 903 Pad, 903 Lip Area, and the Americium Zone.
The Contractor is interested in receiving information on proven
technologies, equipment and methodologies that are applicable to the
remediation of the 903 Pad Area. Remediation Area #1: 903 Pad
(Individual Hazardous Substance Site 112) The area known as the 903 Pad
was formerly used to store drums containing waste oils and chlorinated
solvents contaminated with plutonium, americium and uranium (i.e., the
903 Drum Storage Area). Radionuclide-contaminated oil and solvents
leaked from the drums into the surrounding soils. The drums were
removed in 1968 along with approximately eight inches of contaminated
surface soil. Clean fill and an asphalt pad were then placed over the
remaining contaminated soils. The fill material overlaying the native
soil ranges from 0.3 to 0.9 feet (average of 0.5 feet) in thickness.
The asphalt pad is approximately 400 feet by 400 feet by 0.4 to 0.7
feet (average of 0.5 feet) thick and its surface is relatively level
over its extent. Characterization work conducted in 1998 indicates the
presence of radionuclide contamination in the asphalt pad, fill
material, and native soil beneath the fill material. Contamination of
the asphalt pad and fill material is suspected to have resulted from
wind dispersion of contaminants from the 903 Lip Area. Detected
activities for Pu-239/240, Am-241, U-233/234, U-235, and U-238,
respectively, are as follows (all activities are in pCi/g and ND
indicates non-detect): Asphalt Pad: 0.410 -- 1.22; ND -- 0.341; ND --
1.33; ND -- 0.133; ND -- 0.919 Fill Material: 0.410 -- 558; ND -- 126;
0.728 -- 2.02; 0.029 -- 0.487; 0.844 -- 2.77 Native Soil: ND --
152,000; ND -- 31,670; ND -- 178; ND -- 16.9; ND -- 780
Characterization work indicates the presence of low concentrations of
volatile organic compounds in the native soils beneath the 903 Pad.
These include detections of several regulated chlorinated solvents
including tetrachloroethylene (PCE), trichloroethylene (TCE),
dichloroethylene (DCE) and carbon tetrachloride. Maximum detected
concentrations for these solvents are 6.1 Parts per Million (ppm), 1.5
ppm, 4.4 ppm, and 1.5 ppm, respectively. Preliminary data suggest that
up to 2,500 cubic yards (in place) of native soil beneath the 903 Pad
and fill material are impacted by radiological contamination. The
impacted soils cover an area of up to approximately 2.4 acres and range
from 0.5 to 1.0 feet in depth. Remediation Area #2: 903 Lip Area
(Individual Hazardous Substance Site 155) During the drum removal and
soil cleanup activities conducted at the 903 Drum Storage Area in 1968,
winds and surface water runoff transported contamination beyond the
storage area, primarily to the south and east. This area, bounded by
the interior access roads to the east and south, is designated as the
903 Lip Area. In 1970, approximately six inches of coarse road base was
applied over the native soils in the 903 Lip Area. Targeted soil
cleanup (removal) efforts were undertaken in 1976, 1978, and 1984 in
which soils containing elevated levels of plutonium were removed from
three different areas within the Lip Area. Radionuclide contamination
in the fill material and native soils in the Lip Area remains, however.
Characterization work indicates that plutonium 239/240 activities in
fill and natural soils range from non-detect to 14,950 pCi/g.
Americum-241 activities range from non-detect to 3,140 pCi/g.
Uranium-233/234 activities range from non-detect to 35.8 pCi/g.
Uranium-235 activities range from non-detect to 4.17 pCi/g. Uranium-238
activities range from non-detect to 75.7 pCi/g. Volatile organic
compounds are not expected to be present in the 903 Lip Area.
Preliminary data suggest that up to 10,000 cubic yards (in place) of
903 Lip Area fill/soil are impacted by radiological contamination. The
impacted soils cover an area of up to approximately 6.7 acres and are,
on the average, approximately one foot deep. Remediation Area #3:
Americium Zone Area An area to the east of the 903 Lip Area, designated
as the "Americium Zone," was also impacted during the drum and soil
removal activities conducted in 1968 at the 903 Drum Storage Area. The
Americium Zone is largely comprised of natural soils with the
occasional presence of waste soil piles, concrete, and abandoned soil
monitoring equipment. Characterization data resulting primarily from
soil sampling and analysis and gamma spectroscopy surveys indicate the
presence of the following radionuclide contamination in the Americium
Zone. Plutonium-239/240 is estimated at activities up to 829 pCi/g
(see below). Americum-241 activities range from non-detect to 115.74
pCi/g. Uranium-233/234 has not been detected in the Americium Zone.
Uranium-235 activities range from non-detect to 0.575 pCi/g and
Uranium-238 activities range from non-detect to 11.354 pCi/g. It should
be noted that plutonium was not directly detected in the Americium Zone
(the Pu-239/240 detection limit for direct survey measurements was
2,500 pCi/g). The maximum plutonium activity listed above is
conservatively estimated from detected americium activities using an
Pu-239, 240/Am-241 activity ratio of 7.16. Volatile organic compounds
are not expected to be present in the Americium Zone. Preliminary data
suggest that up to 7,820 cubic yards (in place) of 903 Lip Area
fill/soil are impacted by radiological contamination. The impacted
soils cover an area of up to approximately 9.7 acres and are up to six
inches deep. Geology and Topography: Native soils under the 903 Pad
and in the 903 Lip Area and Americium Zone are primarily clays and
gravel (e.g., gravelly clays, sandy clays, clayey gravel, etc.) with
large cobbles (up to six inches) and large/rocks and boulders (up to
two feet). The portion of the 903 Lip Area to the east of the pad is
relatively flat. The area to the south and southeast of the pad slopes
from the northwest to the southeast at an average grade of
approximately 0.15 feet/feet. The topography of the Americium Zone
varies from flat to gentle slopes to relatively steep hillsides.
Information Packet: A packet containing additional site background
information on the 903 Pad, the 903 Lip Area, and the Americium Zone is
available upon request. The packet includes detailed information on the
historical use of the site and resulting contamination, topography,
geology, and hydrology as well as site characterizations, treatability
studies and removal actions conducted to date. The information packet
also includes scaled maps of the three areas in question that
illustrate the areal extent of contamination and topography. Contact
the point of contact listed at the beginning of this advertisement to
request a copy of the information packet. The information packet will
be sent to those requesting it by regular mail. Source Identification:
As part of a market survey, the Contractor is requesting technical and
operational information regarding technologies, equipment, and methods
that are applicable to the remediation of the 903 Pad, 903 Lip Area,
and Americium Zone. Technologies of interest include, but are not
limited to, soil removal/excavation, handling, conveyance, and
transportation as well as in situ and ex situ soil stabilization
technologies that would effectively reduce the mobility of radiological
contaminants present in soils that may remain in the environment.
Stabilization technologies such as capping, solidification,
vitrification, etc. must significantly reduce the potential for the
contaminants to migrate from the impacted areas via wind and surface
water transport, and must minimize further translocation of these
contaminants into subsurface soils. The Contractor is also interested
in waste minimization technologies. Specifically, technologies and
processes that will minimize the volume of 903 Pad, 903 Lip Area, and
Americium Zone soils that must be disposed in a regulated landfill.
Such technologies include, but are not limited to, size reduction, soil
segregation, soil washing, attrition scrubbing, and compaction.
Technologies that enhance the precision of soil excavation/removal
efforts, and thus, minimize the potential for over-excavation while
achieving remediation targets are also of interest. Because of the
presence and magnitude of the radiological contamination, the
Contractor is interested in technologies and equipment designs that
significantly minimize the generation of dust and dust emissions during
soil removal, transfer, handling, processing, and containerization
activities as well as other remedial field activities. Information
shall include, but not necessarily be limited to: technical
specifications, equipment drawings, process flow-sheets, statements of
qualifications, similar project experience descriptions, operating
performance data, and dust generation/emission data. Due to the nature
of this remediation work, the Contractor is interested in proven
technologies, equipment, and methods for removing/excavating,
transporting/conveying, stabilizing, and processing (for the purpose of
waste minimization) soils contaminated with elevated levels of
hazardous and radionuclide constituents. . All information that the
Offeror considers proprietary and is submitted in response to this
announcement shall be clearly marked, "Proprietary". This Advertisement
is NOT A SOLICITATION for services, equipment or materials. All
submittals shall be received no later than 4:30 P.M. (MST) on October
15, 1999. Submit responses and inquires to Kaiser-Hill Company, L.L.C.,
Rocky Flats Environmental Technology Site, 10808 Highway 93, Unit B,
Golden, Colorado 80403-8200, Attention: Steve Heiman, Building
850.***** Posted 09/16/99 (W-SN380995). (0259) Loren Data Corp. http://www.ld.com (SYN# 0012 19990920\C-0004.SOL)
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