Environmental Engineering Reference
In-Depth Information
• The application of effective urban investigative and geologic forensic techniques
such as conducting a comprehensive site history and the knowledge of contami-
nant fate and transport can identify potential anthropogenic effects at a site.
• Anthropogenic influences may reduce the synergistic effects resulting from cer-
tain combinations of geology and high-risk chemicals. This effect is apparent
where groundwater is shallow, in short supply, and the constructed infrastructure
works to prevent the downward movement of the contamination (e.g., storm sew-
ers and building foundations).
• Anthropogenic infrastructure can influence migration pathways, complicating
environmental investigative and remedial efforts.
• The fate and migration of lead, PCBs, PAHs, and SVOCs released into a geologic
environment of shallow groundwater indicates these compounds did not migrate
a significant distance laterally. Their relative immobility arises from the nature of
the compounds—they have a high soil contaminant risk factor.
• Outdoor storage areas offer potential sites for contaminant release.
• Low points in and around buildings can act as effective conduits of contamina-
tion; sources of contamination were sumps, trenches, and floor drains.
• Successful redevelopment of a damaged site is possible. Here, a city park and con-
version to other land uses is in progress.
14.6 Case Study 5: California
Case Study 5 is located in an urban area in California (DTSC 2006). It became a brownfield
site when shut down after 36 years of operation. According to available records, it was first
developed as a chrome plating facility in 1966 and operated until 1999. Table 14.5 lists some
basic information concerning the site.
TABLE 14.5
Site Characteristics of Case Study 1 Located in California
Characteristic
Site Information
Location
California
Years of operation
36 years
Size of property
2 ac
Geologic setting
Alluvial and fluvial sediments
Soil type and stratigraphy
Sand interbedded with some fine silt and clay
layers.
Contaminants detected
Chromium VI, lead, cadmium, nickel, and mercury
COC for soil
Lead, mercury, cadmium, and chromium VI
COC for groundwater
Chromium VI
Depth to groundwater
Approximately 21 m (70 ft) beneath the surface of
the ground
Highest CRF GW ranking
2300 chromium VI
Highest CRF SOIL ranking
Mercury 15,600
Geovulnerability ranking
63
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