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BEMR
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U.S.
Map
The St. Louis Airport Site Vicinity Properties are located in the cities of
Hazelwood and Berkeley, Missouri. These properties (totaling approximately 80)
include Coldwater Creek and its vicinity properties to the west; adjacent ball
fields to the north and east; Norfolk and Western Railroad properties adjacent
to Coldwater Creek; Banshee Road to the south; ditches to the north and south;
and St. Louis Airport Authority property to the south. Also included are
the transportation routes (haul roads) at the following locations: Latty
Avenue, McDonnell Boulevard, Pershall Road, Hazelwood Avenue, Eva Avenue, Frost
Avenue, and vicinity properties.
LOCALITY MAP
SITE MAP
Estimated Site Total
| (Thousands of Current Year Dollars)
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| |
|
|
|
| Environmental Restoration
|
2,911
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2,909
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4,533
|
5,051
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4,991
|
Grey shaded area reflects annual cost
estimates for the first five years of the site BEMR Base Case (as of October
1995) and includes 3% annual inflation, see Readers' Guide.
|
| 1996 Appropriation
|
7,881
|
|
|
These levels reflect the current estimates for
compliance with applicable statutes and agreements (as of March 1996), see
Readers' Guide.
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| 1997 Congressional Request
|
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7,731
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|
|
| (Five-Year Averages, Thousands of Constant 1996
Dollars)
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| |
2020
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2025
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2030
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| Environmental Restoration
|
3,813
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4,765
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6,680
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4,168
|
|
|
|
97,126
|
| * Total Life Cycle is the sum of the annual costs in
constant FY 1996 dollars.
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FACILITY MISSION
Lowlevel radioactive contamination at the St. Louis Airport Site Vicinity
Properties [estimated at 149,000 cubic meters (195,000 cubic yards)] consists
primarily of soils and sediment contaminated with residues from the processing
of high-grade uranium ore. The contamination at the vicinity properties is
linked to both the St. Louis Airport Site and the Latty Avenue Properties. The
Manhattan Engineer District acquired the St. Louis Airport Site in 1946 and
used it to store uranium-bearing residues from the St. Louis Downtown Site
from 1946 to 1966, when Continental Mining and Milling Company of Chicago
purchased the waste, removed it from the storage site near the airport, and
placed it in storage at Latty Avenue under Atomic Energy Commission license.
Over time, residues migrated from other sites or were deposited when waste was
hauled along transportation routes, and the soils and sediments at the vicinity
properties became contaminated. Commercial enterprises, individuals, or local
governments own the vicinity properties.
FUTURE USE
The final land-use range will depend on the Record of Decision that will
document the remedial action alternative selected for implementation. This
estimate assumes that land use of the vicinity properties will be the same as
the current uses, which range from recreational to industrial/commercial. The
Record of Decision will involve input from the Environmental Protection Agency,
state and local agencies, and stakeholders.
ENVIRONMENTAL RESTORATION
Environmental restoration of the St. Louis Airport site Vicinity Properties is
expected to involve disposition of approximately 149,000 cubic meters
(195,000 cubic yards) of soil. Cleanup will be conducted under the
Comprehensive Environmental Response, Compensation, and Liability Act protocol
for remediation of low-level radioactive contamination at FUSRAP sites and the
Atomic Energy Act of 1954, as amended. Because the site is on the National
Priorities List, a Federal Facilities Agreement negotiated between the
Department and the Environmental Protection Agency incorporates procedural and
documentation requirements of the Comprehensive Environmental Response,
Compensation, and Liability Act and establishes the roles of each agency during
site remediation. As required by the Comprehensive Environmental Response,
Compensation, and Liability Act, development of remediation goals for the site
will incorporate applicable or relevant and appropriate requirements of federal
and state laws.
Key regulators are Environmental Protection Agency Region VII, the
St. Louis Airport Authority, the City of St. Louis, the Missouri
Department of Natural Resources, and local governments as appropriate. Other
regulatory drivers include the Clean Air Act, the Safe Drinking Water Act, and
the National Pollutant Discharge Elimination System.
The schedule for final cleanup depends on the issuance of a Record of Decision
and funding. Waste management strategies will be developed to address pollution
control; waste treatment, storage, disposal, and transportation; interface
requirements; and implementation of new technology.
Major Environmental Restoration Activity Milestones
| Assessment (Record of Decision)
|
1997
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Remedial Action
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2015
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ASSESSMENT
Contaminants at the St. Louis Airport Site Vicinity Properties include
uranium238, radium226, thorium230, and thorium232; the
primary contaminant is thorium230. Based on limited chemical
characterization at the ball field area, no Resource Conservation and Recovery
Act-hazardous characteristic waste is present. Chemical analysis of Coldwater
Creek samples revealed the presence of four metals at concentrations exceeding
both sample detection limits and background levels. Chemical characterization
at the other vicinity properties was deemed unnecessary because of the low
levels of chemical contamination found during characterization at the St. Louis
Airport Site. The Department's present objective at the St. Louis Airport Site
Vicinity Properties is to eliminate or reduce the potential for exposure to
radioactive and chemical contaminants.
The potential for contaminant transport results from the movement of
contaminated soils via surface runoff, ground water, surface water and
sediments, and air. In addition, road and underground utility improvements may
have caused migration of contamination onto adjacent land. Contamination could
spread from the areas along the creek bank that contain elevated radioactivity
if sediment were transported by high flow of the creek or otherwise disturbed;
however, installation of a gabion wall at the eastern bank of the creek has
stabilized creek flow and greatly reduced erosion. Release of contaminants into
the atmosphere appears unlikely because there are currently no operations in
the area that would cause contaminants to become airborne; most areas of
outdoor surface contamination are vegetated, paved, or covered with gravel.
Potential exposure pathways are ingestion and inhalation. Because ground water
is not used as a potable water source in the St. Louis area, the potential
for human exposure via this pathway is minimal. Land use near the St. Louis
Airport Site Vicinity Properties is transportation-related and
Industrial/Commercial; existing sources of contamination do not present a risk
to workers or the public under current land-use conditions.
Radiological characterization at the St. Louis Airport Site Vicinity Properties
began in 1982 and continues in various portions of the site. Radiological
surveys and characterization conducted at the St. Louis Airport Site Vicinity
Properties generally involved establishing a reproducible grid system; clearing
the area to be surveyed; performing gamma radiation walkover scans and
nearsurface gamma radiation measurements; taking direct alpha and
beta-gamma measurements on structure surfaces; collecting and analyzing samples
for radiological and chemical constituents; and collecting and analyzing
geologic and hydrogeologic data to characterize subsurface transport.
Thorium-230 was identified as the primary radioactive contaminant at all St.
Louis Airport Site Vicinity Properties characterized. In general, contamination
was confined to the boundaries of properties adjacent to the haul roads and was
detected to a maximum depth of 0.6 meter (2 feet). Soil sampling
along the haul roads revealed radioactive contamination in areas under Latty
Avenue, McDonnell Boulevard, and Pershall Road; along both sides of Hazelwood
Avenue, Pershall Road, and Eva Avenue; and primarily on the northern side of
Frost Avenue. Radioactive contamination (primarily thorium230) exceeding
guidelines was detected on portions of all the Norfolk and Western Railroad
properties, except the property adjacent to Hanley Road and Hazelwood Avenue,
north of Latty Avenue. Depths of contamination ranged from 0 to 2.1 meters (0
to 7 feet).
The City of St. Louis leases the ball field area north of St. Louis Airport
Site to the City of Berkeley. Analytical results for soil on this property
revealed areas with elevated concentrations of radium226 in surface
samples and thorium230 in both surface and subsurface samples. The
radioactive contamination averages 0.3 meter (1 foot) in depth over the
first 45.7 to 61 meters (150 to 200 feet) along the northern border
of McDonnell Boulevard. The infield areas of the ball fields showed no
contamination.
Elevated concentrations of thorium230 in surface soil samples were
detected in several areas on the St. Louis Airport Authority property to
the south of St. Louis Airport Site. In general, the maximum depth of
contamination was 0.6 meter (2 feet); the extent of contamination
encompassed the length of the property's border with St. Louis Airport Site.
Two small areas with elevated concentrations of thorium230 in soil to a
depth of 0.3 meter (1 foot) were identified at Banshee Road, which
forms the southern boundary of St. Louis Airport Site. Analytical results for
soil at the ditches to the north and south of St. Louis Airport Site revealed
areas with elevated concentrations of radium226 and thorium230 (the
major contaminant) in surface and subsurface samples. Essentially all the ditch
area north and south of St. Louis Airport site is contaminated; the depth of
contamination ranges from 0 to 4.3 meters (0 to 14 feet).
Surface soil and sediment samples from Coldwater Creek and vicinity properties
were collected in 1986 from the sides and center of the creek at 30.5meter
(100foot) intervals beginning at St. Louis Airport Site and continuing
downstream to Hazelwood Interim Storage Site. The data from these analyses
indicated spotty contamination over the entire distance. Analytical results for
sediment revealed areas with elevated concentrations of thorium230, which
is the primary contaminant in Coldwater Creek. Results from the 1987
characterization indicated areas with elevated radium226 and
thorium230 concentrations. During additional characterization in 1989,
soil samples were collected from the banks on both sides of the creek north of
Pershall Road. Radionuclide concentrations were above guidelines in 64 of 175
samples. A 1989 Corps of Engineers survey similarly revealed areas with
thorium230 concentrations exceeding guidelines in surface samples. Areas
of contamination were most numerous between St. Louis Airport Site and Pershall
Road, adjacent to St. Louis Airport Site and Hazelwood Interim Storage Site. A
correlation has been observed between the creek's configuration and the areas
of contamination: above-guideline concentrations of thorium230 appear to
be localized along the inner banks of the creek at the bends, indicating
settling of contaminated sediment. Six of the Coldwater Creek vicinity
properties have thorium230 contamination in excess of guidelines,
primarily in the first foot of soil.
Assessments of contamination are documented as required by the regulatory
process. In addition to the Remedial Investigation/Feasibility
StudyEnvironmental Impact Statement and Record of Decision for the
St. Louis Sites, environmental documentation for St. Louis Airport Site
Vicinity Properties includes a site designation report, a Notice of Intent,
planning documents (work plan, field sampling and analysis plan, quality
assurance plan, community relations plan), and characterization reports.
REMEDIAL ACTION
This report anticipates a phased approach to remedial action, beginning with a
Record of Decision that specifically identifies nearterm actions and
outlines commitments for the future. During an interim removal action at the
St. Louis Airport Site Vicinity Properties in 1995, approximately 1,070 cubic
meters (1,400 cubic yards) of waste was removed from six properties and
shipped to Envirocare of Utah for disposal. Future interim actions are planned
within the next two to three years, to the extent that funding permits. An
Engineering Evaluation/Cost Analysis report and a categorical exclusion report
have documented environmental impacts of interim removal actions that have been
conducted to address contamination on portions of the St. Louis Airport Site
Vicinity Properties before finalization of the Record of Decision.
This report anticipates that a design basis document will be developed to
govern the requirements for the scope of work for final cleanup of the site.
Sitespecific remedial action is expected to include civil survey, material
testing, excavation, and backfill, as well as miscellaneous services such as
water treatment, fence repair, maintenance, trailer setup, mobilization and
demobilization of equipment, handling of contaminated material, janitorial
services, and health physics and analytical laboratory services.
The scenario used for the Baseline Environmental Management Report cost
estimate for the St. Louis Sites assumes excavation of accessible soils
from St. Louis Downtown Site, vicinity properties in the downtown and airport
areas, the Latty Avenue Properties, and sediments at Coldwater Creek, as well
as consolidation and capping at St. Louis Airport Site. The cost estimate
assumes a total waste volume of 149,000 cubic meters (195,000 cubic yards)
of low-level waste at the St. Louis Airport Site Vicinity Properties.
Environmental Restoration Activities Cost Estimate
| (Five-Year Averages, Thousands of Constant 1996
Dollars)
|
| |
2020
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2025
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2030
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| FUSRAP - St. Louis Airport Site Vicinity Properties
|
|
|
|
|
|
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| Assessment
|
40
|
|
|
|
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|
|
200
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| Remedial Action
|
3,773
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4,765
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6,680
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4,168
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|
|
|
96,926
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| Total
|
3,813
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4,765
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6,680
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4,168
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|
|
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97,126
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| * Total Life Cycle is the sum of the annual costs in
constant FY 1996 dollars.
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FUNDING ESTIMATE
The following table presents estimated funding information for the St. Louis
Airport Site Vicinity Properties.
Nondefense Funding Estimate
| (Five-Year Averages, Thousands of Constant 1996
Dollars)
|
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2020
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2025
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2030
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| Environmental Restoration
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3,813
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4,765
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6,680
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4,168
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|
|
|
97,126
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| * Total Life Cycle is the sum of the annual costs in
constant FY 1996 dollars.
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