Environmental Engineering Reference
In-Depth Information
• Not all anthropogenic activities will result in adverse impacts on the environment.
• The degree of environmental impact due to contaminants in a contaminated
ground site is dependent on (a) the nature and distribution of the contaminants,
(b) the various physical, geological, and environmental features of the site, and
(c) existent land use.
• Each type of land use imposes different demands and requirements from the land.
The ideal situation in land utilization matches land suitability with land develop-
ment consistent with environmental sensitivity and sustainability requirements.
• Groundwater is an integral part of land-use considerations.
• Causes and sources of groundwater contamination include wastewater discharges,
injection wells, leachates from landills and surface stockpiles, open dumps and
illegal dumping, underground storage tanks, pipelines, irrigation practices, pro-
duction wells, use of pesticides and herbicides, urban runoff, mining activities, etc.
• To evaluate and determine the nature of geoenvironmental impacts created by the
presence of contaminants in the geoenvironment, one needs to have an apprecia-
tion of the nature of the contaminants and associated events that are responsible
for the impacts. The various activities associated with the production of goods
and services generate waste streams and products. In most instances, these waste
streams and products ind their way into the land environment, either inadver-
tently as in the case of runoffs and spills or by design, i.e., failure of constructed
safe land disposal facilities.
References
Agency for Toxic Substances and Disease Registry (ATSDR). (1999), Toxicological Proile for
Cadmium, Atlanta, GA: U.S. Department of Health and Human Services, Public Health Service.
Appelo, C.A.J. and Postma, D. (1993), Geochemistry, Groundwater and Pollution , Balkema, Rotterdam,
536 pp.
Chiou, G.T., Schmedding, D.W., and Manes, M. (1982), Partition of organic compounds on octanol-
water system, Environmental Science & Technology , 16:4-10.
Fetter, C.W. (1993), Contaminant Hydrogeology , Macmillan Publishing Co., New York, 458 pp.
Greenland, D.G. and Hayes, M.H.B. (eds.) (1981), The Chemistry of Soil Processes , John Wiley & Sons,
New York, 714 pp.
Huang, P.M., Berthelin, J., Bollag, J.-M., McGill, W.B., and Page, A.L. (eds.) (1995a), Environmental
Impact of Soil Component Interactions: Natural and Anthropogenic Organics , CRC Press, Boca Raton,
FL, 450 pp.
Huang, P.M., Berthelin, J., Bollag, J.-M., McGill, W.B., and Page, A.L. (eds.) (1995b), Environmental
Impact of Soil Component Interactions: Metals, Other Inorganics, and Microbial Activities , CRC Press,
Boca Raton, FL, 263 pp.
Karlen, D.L., Mausbach, M.J., Doran, J.W., Cline, R.G., Harris, R.F., and Schuman, G.E. (1997), Soil
quality: A concept, deinition, and framework for evaluation, Soil Science Society of America
Journal , 61:4-10.
Knox, R.C., Sabatini, D.A., and Canter, L.W. (1993), Subsurface Transport and Fate Processes , Lewis,
Boca Raton, FL, 430 pp.
Lewis, D.R., Southwick, J.W., Ouellet-Hellstrom, R., Rench, J. and Calderon, R.L. (1999), Drinking
water arsenic in Utah: A cohort mortality study, Environmental Health Perspectives , 107:359-365.
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