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First of all, from the scale of each city, the water ecological carrying capacity (ECC) was calculated from 2000 to 2011, and map the spatial distribution of the recent 3 years which show that, the water ecological carrying capacity (ECC) is uneven and has a downward trend year by year.
Our findings highlight the need for efficient multi-scale monitoring strategies in geologically heterogeneous lowland stream/aquifer systems in order to more adequately quantify the risk to surface water ecological receptors posed by point-source groundwater contaminants like TCE.
The multi-compensation measures and schemes in both temporal and spatial scales are outlined in this paper and this study provides new theories on and methods for water ecological compensation in coal mining areas where reconstruction is needed.
A graphical user interface written in Visual C++ provides powerful inventory analysis tools, dialogs for selecting timber, water, ecological, wildlife, and visual goals, and dialogs for defining treatments and building prescriptive management plans.
Therefore, considering all the retrospective studies mentioned above, there is little evidence to suggest that surfactants as a whole (e.g., mixture) are primary stressors on receiving water ecological communities which supports the conclusions of the prospective risk assessment (Section VI).
Furthermore, these studies show the PEC/PNEC ratios for surfactants to be below unity, indicating that there is little evidence to suggest that surfactants are a primary driver of receiving water ecological status.
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Performance of a stochastic-dynamic modelling methodology for running waters ecological assessment.
Considering its resemblance to the blacktip reef shark, the smoothtooth blacktip shark may play an equivalent shallow-water ecological role within its range.
Since all early Mesozoic records of Scleractinia represent rather shallow-water ecological settings, it is not yet possible to infer whether the Scleractinia were initially abyssal and then colonized shallow waters (as hypothesized by Lindner et al. [42] for the stylasterid corals), or vice-versa.
In contrast, for arsenic in drinking-water, ecological studies provide important information on causal inference, because of large exposure contrasts and limited population migration.
We demonstrate the advisability of addressing water-ecological problems on the basis of a knowledge of the formation regularities of hydrological processes with the use of the method of indication and typology.
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