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1

Commission, International Joint. Literature review of the effects of persistent toxic substances on Great Lakes biota: Report of the Health of Aquatic Communities Task Force. International Joint Commission, 1986.

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2

Patterns and factors of biota distribution in remote European mountain lakes. Schweizerbart, 2009.

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3

Oceans, Canada Department of Fisheries and. Acidification of surface waters in eastern Canada and its relationship to aquatic biota. Department of Fisheries and Oceans, 1987.

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4

Stephenson, Malcolm. Carbon-14 activity in the water, sediments and biota of lakes 226 North, 226 South and 224, experimental lakes area, 1989 to 1994. AECL, Whiteshell Laboratories, 1994.

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5

Fitchko, Yaroslaw. Literature review of the effects of persistent toxic substances on Great Lakes biota: Report of the Health of Aquatic Communities Task Force. International Joint Commission, Great Lakes Regional Office, 1986.

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6

International Joint Commission. Great Lakes Science Advisory Board. Literature Review of the Effects of Persistent Toxic Substances on Great Lakes Biota: Report of the Health of Aquatic Communities Task Force. s.n, 1986.

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7

Thodal, Carl E. Field screening of water quality, bottom sediment, and biota associated with irrigation in and near the Indian Lakes area, Stillwater Wildlife Management area, Churchill County, West-Central Nevada, 1995. U.S. Dept. of the Interior, U.S. Geological Survey, 1998.

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8

Setmire, James G. Reconnaissance investigation of water quality, bottom sediment, and biota associated with irrigation drainage in the Salton Sea area, California, 1986-87. Dept. of the Interior, U.S. Geological Survey, 1990.

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9

Schroeder, Roy A. Reconnaissance investigation of water quality, bottom sediment, and biota associated with irrigation drainage in the Tulare Lake bed area, southern San Joaquin Valley, California, 1986-87. Dept. of the Interior, U.S. Geological Survey, 1988.

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10

M, Kelso J. R., ed. Acidification of surface waters in eastern Canada and its relationship to aquatic biota. Dept. of Fisheries and Oceans, 1986.

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11

Kirchman, David L. Dead Zones. Oxford University Press, 2021. http://dx.doi.org/10.1093/oso/9780197520376.001.0001.

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This book explores the many rivers, lakes, and oceans that are losing oxygen. Aquatic habitats with little dissolved oxygen are called dead zones because nothing can live there except some microbes. The number and size of dead zones are increasing worldwide. The book shows that oxygen loss causes fish kills, devastates bottom-dwelling biota, reduces biological diversity, and rearranges aquatic food webs. In the 19th century in rich countries and in poor regions today, dead zones are accompanied by waterborne diseases that kill thousands of people. The open oceans are losing oxygen because of climate change, whereas dead zones in coastal waters and seas are caused by excessive nutrients, which promote excessive growth of algae and eventually oxygen depletion. Work by Gene Turner and Nancy Rabalais demonstrated that nutrients in the Gulf of Mexico come from fertilizers used in the US Midwest, home to the most productive cropland in the world. Agriculture is also the biggest source of nutrients fuelling dead zones in the Baltic Sea and other coastal waters. Today, fertilizers contaminate drinking water and kick-start harmful algal blooms in local lakes and reservoirs. Nutrient pollution in some regions has declined because of buffer zones, cover crops, and precision agriculture, but more needs to be done. The book concludes by arguing that each of us can do our part by changing our diet; eating less, especially eating less red meat, would improve our health and the health of the environment. A better diet could reduce the amount of greenhouse gas emitted by agriculture and shrink dead zones worldwide.
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12

Vuorinen, Ilppo. Post-Glacial Baltic Sea Ecosystems. Oxford University Press, 2018. http://dx.doi.org/10.1093/acrefore/9780190228620.013.675.

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Post-glacial aquatic ecosystems in Eurasia and North America, such as the Baltic Sea, evolved in the freshwater, brackish, and marine environments that fringed the melting glaciers. Warming of the climate initiated sea level and land rise and subsequent changes in aquatic ecosystems. Seminal ideas on ancient developing ecosystems were based on findings in Swedish large lakes of species that had arrived there from adjacent glacial freshwater or marine environments and established populations which have survived up to the present day. An ecosystem of the first freshwater stage, the Baltic Ice Lake initially consisted of ice-associated biota. Subsequent aquatic environments, the Yoldia Sea, the Ancylus Lake, the Litorina Sea, and the Mya Sea, are all named after mollusc trace fossils. These often convey information on the geologic period in question and indicate some physical and chemical characteristics of their environment. The ecosystems of various Baltic Sea stages are regulated primarily by temperature and freshwater runoff (which affects directly and indirectly both salinity and nutrient concentrations). Key ecological environmental factors, such as temperature, salinity, and nutrient levels, not only change seasonally but are also subject to long-term changes (due to astronomical factors) and shorter disturbances, for example, a warm period that essentially formed the Yoldia Sea, and more recently the “Little Ice Age” (which terminated the Viking settlement in Iceland).There is no direct way to study the post-Holocene Baltic Sea stages, but findings in geological samples of ecological keystone species (which may form a physical environment for other species to dwell in and/or largely determine the function of an ecosystem) can indicate ancient large-scale ecosystem features and changes. Such changes have included, for example, development of an initially turbid glacial meltwater to clearer water with increasing primary production (enhanced also by warmer temperatures), eventually leading to self-shading and other consequences of anthropogenic eutrophication (nutrient-rich conditions). Furthermore, the development in the last century from oligotrophic (nutrient-poor) to eutrophic conditions also included shifts between the grazing chain (which include large predators, e.g., piscivorous fish, mammals, and birds at the top of the food chain) and the microbial loop (filtering top predators such as jellyfish). Another large-scale change has been a succession from low (freshwater glacier lake) biodiversity to increased (brackish and marine) biodiversity. The present-day Baltic Sea ecosystem is a direct descendant of the more marine Litorina Sea, which marks the beginning of the transition from a primeval ecosystem to one regulated by humans. The recent Baltic Sea is characterized by high concentrations of pollutants and nutrients, a shift from perennial to annual macrophytes (and more rapid nutrient cycling), and an increasing rate of invasion by non-native species. Thus, an increasing pace of anthropogenic ecological change has been a prominent trend in the Baltic Sea ecosystem since the Ancylus Lake.Future development is in the first place dependent on regional factors, such as salinity, which is regulated by sea and land level changes and the climate, and runoff, which controls both salinity and the leaching of nutrients to the sea. However, uncertainties abound, for example the future development of the Gulf Stream and its associated westerly winds, which support the sub-boreal ecosystems, both terrestrial and aquatic, in the Baltic Sea area. Thus, extensive sophisticated, cross-disciplinary modeling is needed to foresee whether the Baltic Sea will develop toward a freshwater or marine ecosystem, set in a sub-boreal, boreal, or arctic climate.
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13

United States. Bonneville Power Administration. Division of Fish and Wildlife., ed. Measurement of Lake Roosevelt biota in relation to reservoir operations: Final report 1993. Bonneville Power Administration, 1996.

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14

C, Scudder Barbara, National Water-Quality Assessment Program (U.S.), and Geological Survey (U.S.), eds. Trace elements and synthetic organic compounds in biota and streambed sediment of the Western Lake Michigan Drainages, 1992-1995. U.S. Dept. of the Interior, U.S. Geological Survey, 1997.

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15

Detailed study of selenium in glacial-lake deposits, wetlands, and biota associated with irrigation drainage in the southern Freezeout Lake area, west-central Montana, 1994-95. U.S. Geological Survey, 1999.

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16

Eloise, Kendy, and Geological Survey (U.S.), eds. Detailed study of selenium in glacial-lake deposits, wetlands, and biota associated with irrigation drainage in the southern Freezeout Lake area, west-central Montana, 1994-95. U.S. Dept. of the Interior, U.S. Geological Survey, 1999.

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17

Eloise, Kendy, and Geological Survey (U.S.), eds. Detailed study of selenium in glacial-lake deposits, wetlands, and biota associated with irrigation drainage in the southern Freezeout Lake area, west-central Montana, 1994-95. U.S. Dept. of the Interior, U.S. Geological Survey, 1999.

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18

Detailed study of selenium in soil, water, bottom sediment, and biota in the Sun River Irrigation Project, Freezout Lake Wildlife Management Area, and Benton Lake National Wildlife Refuge, west-central Montana, 1990-92. The Survey, 1996.

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19

A, Nimick David, and Geological Survey (U.S.), eds. Detailed study of selenium in soil, water, bottom sediment, and biota in the Sun River Irrigation Project, Freezout Lake Wildlife Management Area, and Benton Lake National Wildlife Refuge, west-central Montana, 1990-92. The Survey, 1996.

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20

Detailed study of selenium in soil, water, bottom sediment, and biota in the Sun River Irrigation Project, Freezout Lake Wildlife Management Area, and Benton Lake National Wildlife Refuge, west-central Montana, 1990-92. The Survey, 1996.

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21

1946-, Butler David L., Geological Survey (U.S.), U.S. Fish and Wildlife Service, and United States. Bureau of Reclamation, eds. Reconnaissance investigation of water quality, bottom sediment, and biota associated with irrigation drainage in the Gunnison and Uncompahgre River basins and at Sweitzer Lake, west-central Colorado, 1988-89. U.S. Dept. of the Interior, U.S. Geological Survey, 1992.

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