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Aquatic Park

Dredging Paradise The Making of San Diego s Mission Bay Aquatic Park... [Pg.1147]

Mission Bay Aquatic Park A New Scale of Shoreline Transformation... [Pg.1151]

Gabrielson, E. (2002). Mission Bay aquatic park The history of planning and land acquisitions. The Journal of San Diego History, 48 ), 1-7. [Pg.1158]

Rencz AN, O Driscoll NJ, Hall GEM, Peron T, Tehner K, Burgess NM. 2003. Spatial variation and correlations of mercury levels in the terrestrial and aquatic components of a wetland dominated ecosystem Kejimkujik Park, Nova Scotia, Canada. Water Air Soil PoUut 143 271-288. [Pg.119]

Mabey WR, Smith JH, Podoll RT, et al. 1982. Aquatic fate process data for organic priority pollutants. Report to U.S. Environmental Protection Agency, Office of Water Regulations and Standards, Washington, DC, by SRI International, Menlo Park, CA. EPA 440/4-81-014. [Pg.123]

Logarithmic bioconcentration factors have been shown to be correlated with the logarithmic octa-nol/water partition coefficient in aquatic organisms (Davies and Dobbs, 1984 de Wolf et al., 1992 Isnard and Lambert, 1988) and fish (Davies and Dobbs, 1984 Kenaga, 1980 Isnard and Lambert, 1988 Neely et al., 1974 Ogata et al., 1984 Oliver and Niimi, 1985). In addition, bioconcentration factors are well correlated by a linear solvation energy relationship (coimnonly known as LSER) that includes the intrinsic solute molecular volume and solvatochromic parameters that measnre hydrogen bond acceptor basicity and donor acidity of the componnd (Park and Cho, 1993). [Pg.17]

Ortlepp J, Miirle U (2003) Effects of experimental flooding on brown trout (Salmo trutta fario L.) The River Spol, Swiss National Park. Aquat Sci 65 232... [Pg.226]

A. Samecka-Cymerman, A. Stankiewicz, K. Kolon and A. J. Kempers, Self-organizing feature map (neural networks) as a tool in classification of the relations between chemical composition of aquatic bryophytes and types of streambeds in the Tatra national park in Poland, Chemosphere, 67(5), 2007, 954-960. [Pg.281]

Water Pollution Control Act of 1972, as Amended by Clean Water Act of 1977 , Environment Reporter, Fed Laws 71 (Dec 8,1978), 5101 ff 41) D.H.W. Liu et al, Toxicity of TNT Waste-waters to Aquatic Organisms. Vol I. Acute Toxicity of LAP Wastewater and 2,4,6-Trinitrotoluene , Final Rept, Contract DAMD 17-75-C-5056, SRI International, Menlo Park, Ca (1978) 42) H.V. Ellis et al, Mammalian... [Pg.838]

McCart, E., A. M. Gordon, N. K. Kaushik, B. Lazerte, E. Mallory, R. W. Bachmann, J. R. Jones, R. H. Peters, and D. M. Soballe. 1995. Characterization of selected allochthonous organic carbon inputs within a terrestrial-aquatic ecotone in Algonquin Park, Ontario. Lake Reserve Management 11 168. [Pg.65]

FIGURE 7 Diagram of C N vs. AR AL-I, where AR AL-I is the ratio of aromatic (AR) to aliphatic (AL-I) carbons, as determined from a quantitative 13C-NMR spectrum. The solid line is a simple linear regression (r2 = 0.52, n = 14, p = 0.003). The position of fulvic acids collected in Rocky Mountain National Park in Colorado is shown relative to other aquatic fulvic acids (from McKnight cl al., 1997). SO, Sky Pond Outlet AC, Andrews Creek IB, Icy Brook LO, Loch Vale Outlet. Other fulvic acids are described in McKnight et al. (1992 and 1994). [Pg.85]

Park, J. C., M. Aizaki, T. Fukushima, and A. Otsuki. 1997. Production of labile and refractory dissolved organic carbon by zooplankton excretion An experimental study using large outdoor continuous flow-through ponds. Canadian Journal of Fisheries and Aquatic Sciences 54 434—443. [Pg.118]

If, through a proper landscape analysis, a realistic combination of multiple stressors is identified, food-web models may be used to predict and extrapolate their ecological effects to relevant ecosystems of the landscape unit of concern. An overview of models that can be used for the integrated assessment of eutrophication and organic contaminants in aquatic ecosystems is provided by Koelmans et al. (2001). Examples of aquatic food-web models that can be used or adapted to predict effects of multiple stressors are IFEM (Bartell et al. 1988), AQUATOX (Park 1999), and C-COSM (Traas 2004). [Pg.250]

Park RA] US Environmental Protection Agency. 1999. AQUATOX for Windows a modular toxic effects model for aquatic ecosystems [computer program], Washington (DC) US Environmental Protection Agency, http //www.epa.gov/ost/models/aquatox/ (accessed December 28, 2007). [Pg.352]


See other pages where Aquatic Park is mentioned: [Pg.1147]    [Pg.1149]    [Pg.1151]    [Pg.1151]    [Pg.1153]    [Pg.1155]    [Pg.1156]    [Pg.1157]    [Pg.1157]    [Pg.2285]    [Pg.1147]    [Pg.1149]    [Pg.1151]    [Pg.1151]    [Pg.1153]    [Pg.1155]    [Pg.1156]    [Pg.1157]    [Pg.1157]    [Pg.2285]    [Pg.11]    [Pg.39]    [Pg.49]    [Pg.317]    [Pg.838]    [Pg.5]    [Pg.437]    [Pg.62]    [Pg.68]    [Pg.131]    [Pg.204]    [Pg.272]    [Pg.1388]    [Pg.156]    [Pg.24]    [Pg.553]    [Pg.101]    [Pg.102]    [Pg.152]    [Pg.31]    [Pg.75]   
See also in sourсe #XX -- [ Pg.1147 , Pg.1148 , Pg.1149 , Pg.1150 , Pg.1151 , Pg.1152 , Pg.1153 , Pg.1154 , Pg.1155 , Pg.1156 ]




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