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Air Pollution Threats to US National Parks of the Great Lakes Region

Published online by Cambridge University Press:  24 August 2009

Thomas V. Armentano
Affiliation:
Director, Biotic Resource Analysis Program, Holcomb Research Institute, Butler University, 4600 Sunset Avenue, Indianapolis, Indiana 46208, USA
Orie L. Loucks
Affiliation:
Director, Holcomb Research Institute, Butler University, 4600 Sunset Avenue, Indianapolis, Indiana 46208, USA.

Extract

The Great Lakes region of the interior of North America supports a large human population, a major industrial base, and recreational and scenic amenities of unusual contrast and quality. To protect portions of this landscape and meet national recreational needs, the US Federal Government has established 10 National Parks, Monuments, and Lakeshores, in the region, extending from northern Minnesota to the southern shore of Lake Erie. However, air pollutant sources from the industrial Midwest, and large-scale coal combustion for electricity along the Ohio Valley, show evidence of significantly threatening the resource qualities protected in these parks.

A review of the natural resources and amenities in each of the National Parks, Monuments, and Lakeshores, in the region shows that scenic vistas are of primary significance, with unique biota (largely northern coniferous species and associated bird-life) and clear water also prominent. Pollutant concentrations in the southern sites, however, are above the thresholds that are known to produce stress, foliage damage, and altered growth-rates on many sensitive species, including the coniferous trees. These pollutants include gases such as sulphur dioxide and nitrogen oxides (NOX) that are primary emissions of relatively local origin, as well as pollutants such as sulphate particulates, ozone, and acidic deposition, produced by chemical transformations during long-distance atmospheric transport. The particulates, in combination with the high average summer humidity, produce a reduction of visibility at the southern sites, and hence the partial loss of an important amenity.

Type
Main Papers
Copyright
Copyright © Foundation for Environmental Conservation 1983

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References

REFERENCES

Council On Environmental Quality (1978). Environmental Quality. The 9th Annual Report of the Council on Environmental Quality, Washington, DC, USA: 599 pp., illustr.Google Scholar
Council On Environmental Quality (1979). Environmental Quality. The 10th Annual Report of the Council on Environmental Quality, Washington, DC, USA: 816 pp., illustr.Google Scholar
Council On Environmental Quality (1980). Environmental Quality. The 11th Annual Report of the Council on Environmental Quality, Washington, DC, USA: 497 pp., illustr.Google Scholar
Cowles, H.C. (1899). Ecological relations of the vegetation on sand dunes of Lake Michigan. Botanical Gazette, 27, pp. 361–88, illustr.CrossRefGoogle Scholar
Dochinger, L.S., Bender, F.W., Fox, F.L. & Heck, W.W. (1970). Chlorotic dwarf of eastern White Pine caused by an ozone and sulphur dioxide interaction. Nature (London), 225, p. 476, illustr.CrossRefGoogle ScholarPubMed
Ferman, M.A., Wolff, G.T. & Kelly, N.A. (1981). The nature and sources of haze in the Shenandoah Valley/Blue Ridge Mountains area. APCA Journal, 31(10), pp. 1074–82, illustr.Google Scholar
Galloway, J.N. & Cowling, E.B. (1978). The effects of precipitation on aquatic and terrestrial ecosystems: A proposed precipitation chemistry network. APCA Journal, 28(3), pp. 229–35, illustr.Google Scholar
Glass, G.E. (1980). Susceptibility of aquatic and terrestrial resources of Minnesota, Wisconsin, and Michigan, to impacts from acid precipitation: Informational requirements. Pp 112–3 in Ecological Impact of Acid Precipitation (Ed. Drablos, D. & Tollan, A.). (Proceedings of an international conference, Sandefjord, Norway: SNSF Project, Oslo-A's, Norway, 1980.) Grefslie Trykkeri, Mysen, Norway: 383 pp., illustr.Google Scholar
Glass, G.E. & Loucks, O.L. (Ed.) (1980). Impacts of Airbone Pollutants on Wilderness Areas along the Minnesota-Ontario Border. US Environmental Protection Agency, EPA-600/ 3-80-044, Washington, DC, USA: 187 pp., illustr.Google Scholar
Harvey, H.H., Pierce, R.C., Dillon, P.J., Kramer, J.P. & Whelpdale, D.M. (1981). Acidification in the Canadian Aquatic Environment: Scientific Criterion for an Assessment of the Effects of Acidic Deposition on Aquatic Ecosystems. Nat. Res. Coun. Canada, Report No. 18475, 369 pp., illustr.Google Scholar
Hileman, B. (1982). Crop losses from air pollutants. Environ. Sci. and Technol., 16, pp. 495A–9A, illustr.CrossRefGoogle ScholarPubMed
Houston, D.B. (1974). Responses of selected Pinus strobus L. clones to fumigations with sulfur dioxide and ozone. Canadian Journal of Forest Research, 4, pp. 65–8, illustr.CrossRefGoogle Scholar
Husar, R.B., Holloway, J.M., Patterson, D.E. & Wilson, W.E. (1981). Spatial and temporal pattern of eastern US haziness: A summary. Atmospheric Environment, 15(10/11), pp. 1919–28, illustr.CrossRefGoogle Scholar
Karnosky, D.F. (1976). Threshold levels for foliar injury to Populus tremuloides by sulfur dioxide and ozone. Canadian Journal of Forest Research, 6(2), pp. 166–9, illustr.CrossRefGoogle Scholar
Karnosky, D.F. (1980). Changes in southern Wisconsin White Pine stands related to air pollution sensitivity. P. 238 in International Symposium on Effects of Air Pollutants on Mediterranean and Temperate Forest Ecosystems. (Riverside, California, USA, 22–27 June 1980: US Dept Agric. Forest Service, Gen. Tech. Rep. PSW-43.) Pacific Southwest Forest and Range Exp. Station, Berkeley, California, USA: 256 pp., illustr.Google Scholar
Kohut, R.J., Krupa, S.V. & Russo, F. (1977). An open-top field-chamber study to evaluate the effects of air pollutants on soybean yields. Proceedings American Phytopathology Society, 4, 88 pp., illustr.Google Scholar
Kress, K.W. & Skelly, J.M. (1982). Response of several eastern forest tree species to chronic doses of ozone and nitrogen dioxide. Plant Disease (formerly Plant Disease Reporter), 66, pp. 1149–52, illustr.CrossRefGoogle Scholar
Legge, A.H. (1980). Primary productivity, sulfur dioxide, and the forest ecosystem: An overview of a case study. Pp. 5162 in International Symposium on Effects of Air Pollutants on Mediterranean and Temperate Forest Ecosystems. (Riverside, California, USA, 22–27 June 1980: US Dept Agric. Forest Service, Gen. Tech. Rep. PSW-43.) Pacific Southwest Forest and Range Exp. Station, Berkeley, California, USA: 256 pp., illustr.Google Scholar
Likens, G.E. (1976). Acid precipitation. Chemical and Engineering News, 54, pp. 2944, illustr.CrossRefGoogle Scholar
Lioy, P.J. & Samson, P.J. (1979). Ozone concentration patterns observed during the 1976–77 long-range transport study. Environment International, 2, pp. 7783, illustr.CrossRefGoogle Scholar
Loucks, O.L., Miller, R.W. & Armentano, T.V. (1982). Regional Assessment of Aquatic Resources at Risk from Acidic Deposition. (Report to the Office of Technology Assessment, US Congress.) The Institute of Ecology, Indianapolis, Indiana, USA: 108 pp.Google Scholar
National Research Council Committee on the Atmosphere and the Biosphere (1981). Atmosphere-Biosphere Interactions: Toward a Better Understanding of the Ecological Consequences of Fossil Fuel Combustion. Commission on Natural Resources, National Academy Press, Washington, DC, USA: 263 pp.Google Scholar
Skelly, J.M., Duchelle, S. & Kress, L.W. (1979). Impact of photochemical oxidant to White Pine in the Shenandoah, Blue Ridge Parkway, and Great Smoky Mountain National Park. P. 131 in Second Conference on Scientific Research in the National Parks. American Institute of Biological Sciences and National Park Service [not available for checking].Google Scholar
Stottlemyer, J.R. (1982). The neutralization of acid precipitation in watershed ecosystems of the Upper Peninsula of Michigan. Pp. 261–75 in Acid Precipitation Effects on Ecological Systems (Ed. D'Itri, F.M.). Ann Arbor Science, Ann Arbor, Michigan, USA: 506 pp., illustr.Google Scholar
Townsend, A.M. & Dochinger, L.S. (1974). Relationship of seed source and developmental stage to the ozone tolerance of Acer rubrum seedlings. Atmospheric Environment, 8, pp. 957–64, illustr.CrossRefGoogle Scholar
Treshow, M. & Stewart, D. (1973). Ozone sensitivity of plants in natural communities. Biological Conservation, 5, pp. 209–14, illustr.CrossRefGoogle Scholar
Trijonis, J. & Shapland, D. (1978). Existing Visibility Levels in the US, Isopleth Maps of Visibility in Suburban/Non-urban Areas During 1974–76. EPA 450/5-79-101, Research Triangle Park, North Carolina, USA: illustr. [Not available for checking.]Google Scholar
Ulrich, B., Mayer, R. & Khanna, P.K. (1980). Chemical changes due to acid precipiation in a loess-derived soil in central Europe. Soil Science, 130(4), pp. 193–9, illustr.CrossRefGoogle Scholar
U.S./Canada (1979). The LRTAP Problem in North America: A Preliminary Overview. (Report of the United States—Canada Research Consultation Group on the Long-Range Transport of Air Pollutants, Co-chaired by A.P. Altshuller & G.A. McBean.) USA State Department and Canada Department of External Affairs: 48 pp., illustr.Google Scholar
U.S. Environmental Protection Agency (1979). Protection Visibility: An EPA Report to Congress. EPA-450/5-79-008, Research Triangle Park, North Carolina, USA: illustr. [Not available for checking.]Google Scholar
Usher, R.W. & Williams, W.T. (1982). Air toxicity to Eastern White Pines in Indiana. Plant Disease Reporter, 66, pp. 199204, illustr.CrossRefGoogle Scholar
Weiss, R.E., Waggoner, A.P., Charson, R.J. & Ahlquist, N.C. (1977). Sulfate aerosol: Its geographical extent in the midwestern and southern United States. Science, 195, pp 979–81, illustr.CrossRefGoogle ScholarPubMed
Wolff, G.T., Lioy, P.J. & Wight, G.D. (1980). Transport of ozone associated with an air-mass. Journal of Environmental Science and Health, A15(2), pp. 183–9, illustr.Google Scholar