Environmental Engineering Reference
In-Depth Information
than its trivalent form—and has greater potential to damage the environment and impact
human health. This is especially significant since hexavalent chromium has a high con-
taminant risk factor, which will be examined in great detail in Chapter 10. Significantly
high contamination ratios were demonstrated by Cr, Cd, and Pb within the watershed's
sand unit, but there were also several metals detected at concentrations exceeding their
MCLs in clay-related soil units, indicating the existence of some mobility within a soil
medium previously considered virtually immobile for metals.
These findings create considerable environmental concern because of the hydraulic con-
nection between the watershed's surface waters and the Great Lakes. Moreover, many
private and public wells use the groundwater within the region for potable water, thus
creating a potential public health risk.
In the next chapter, a model is developed and applied within an urbanized watershed to
help predict the risks posed by specific contaminants to soils, groundwater, and air.
References
Alkhatib, E. and T. O'Connor, 1998. Background levels of priority pollutant metals in soil. American
Environmental Laboratory 10:6-9.
Bedient, P.B., R.S. Hanadi, and C.J. Newell. 1994. Ground Water Contamination . Englewood Cliffs, NJ:
Prentice Hall.
Dowdy, R.H. and V.V. Volk. 1983. Movement of heavy metals in soil. In Chemical Mobility and
Reactivity in Soil Systems , Journal of the Soil Science Society of America, pp. 229-239. Madison,
WI.
Farrand, W.R. 1982. Quaternary Geology of Southern (& Northern) Michigan . Michigan Department of
Natural Resources, Geological Survey Division. Lansing, MI. 1:500,000, 2 Sheets.
Farrand, W.R. 1988. The Glacial Lakes around Michigan . Michigan Department of Natural Resources
Bulletin. 4. Lansing, MI.
Fetter, C.W. 1993. Contaminant Hydrogeology , 2nd edn. Upper Saddle River, NJ: Prentice Hall.
Freeze, R.A. and J.A. Cherry. 1979. Groundwate r. Englewood Cliffs, NJ: Prentice-Hall.
Harter, R.D. and R.G. Lehmann. 1983. Use of kinetics for the study of exchange reactions in soils.
Journal of the Soil Science Society of America 47:666-669.
Jaagumagi, R. 1993. Development of the Ontario Provincial Sediment Quality Guidelines for Arsenic ,
Cadmium , Chromium , Copper , Iron , Lead , Manganese , Mercury , Nickel and Zinc . Toronto, ON:
Ontario Ministry of the Environment.
Kaufman, M.M., K.S. Murray, and D.T. Rogers. 2003. Surface and subsurface geologic risk factors to
groundwater affecting brownfield redevelopment potential. Journal of Environmental Quality
32:490-499.
Keller, K.C., G. Van Der Camp, and J.A. Cherry. 1989. A multiscale study of the permeability of a thick
clay till. Water Resources Research 25:2299-2317.
Keller, K.C., G. Van Der Camp, and J.A. Cherry. 1991. Hydrogeochemistry of a clayey till: Spatial
variability. Water Resources Research 27:2543-2554.
Krishan, P. 1997. Chromium Toxicity Effects on Microorganisms and Treatment Processes . NTIS:
DE00761432. College Station, TX: Texas A&M University.
Lindsay, W.L. 1979. Chemical Equilibria in Soils . New York: John Wiley and Sons.
Mattigod, S.V., G. Sposito, and A.L. Page. 1981. Factors affecting the solubilities of trace metals in
soils. In Chemistry in the Soil Environment , ed. D.E. Baker, pp. 203-221. ASA Special Publication
Number. 40. American Society of Agronomy. Madison, WI.
McLean, J.E. and B.E. Bledsoe, 1992. Ground Water Issue Behavior of Metals in Soils . Technology
Innovation Office. Office of Solid Waste and Emergency Response. Washington, DC: USEPA.
 
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