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Pollution environmental risk assessment

Herbicides constitute a large and diverse class of pesticides that, with a few exceptions, have very low mammalian toxicity and have received relatively little attention as environmental pollutants. Much of the work in the held of ecotoxicology and much environmental risk assessment has focused on animals, especially vertebrate animals. There has perhaps been a tendency to overlook the importance of plants in the natural world. Most plants belong to the lowest trophic levels of ecosystems, and animals in higher trophic levels are absolutely dependent on them for their survival. [Pg.257]

Apart from the use of this approach to study the ecotoxicology of neurotoxic pollutants in the field, it also has potential for use during the course of environmental risk assessment. An understanding of the relationship between biomarker responses to neurotoxic compounds and effects at the population level can be gained from both field studies and the use of mesocosms and other model systems. From these it may be possible to define critical thresholds in biomarker responses of indicator species above which population effects begin to appear. In the longer term, this approach... [Pg.316]

At the practical level, an ideal mechanistic biomarker should be simple to use, sensitive, relatively specific, stable, and usable on material that can be obtained by nondestructive sampling (e.g., blood or skin). A tall order, no doubt, and no biomarker yet developed has all of these attributes. However, the judicious use of combinations of biomarkers can overcome the shortcomings of individual assays. The main point to emphasize is that the resources so far invested in the development of biomarker technology for environmental risk assessment has been very small (cf the investment in biomarkers for use in medicine). Knowledge of toxic mechanisms of organic pollutants is already substantial (especially of pesticides), and it grows apace. The scientific basis is already there for technological advance it all comes down to a question of investment. [Pg.324]

Application of the Preliminary Pollutant Limit Value (PPLV) Environmental Risk Assessment Approach to Selected Land Uses... [Pg.263]

The output of an exposure and risk assessment will usually describe the levels of exposure and quantity the population exposed for both humans and other biota, and will estimate the associated probabilities of the incidence of adverse health effects. Population exposure or risk, obtained by multiplying the individual (per capita) exposure or risk by the numbers exposed at each level of exposure, may also be a useful measure of impact. Various analyses can be performed on the results, for example, comparison of exposures in a particular geographic area against national average exposure levels. Likewise, for the same pollutant, environmental risks due to a particular industry might be compared against risks associated with occupational or household activities. In addition, the health risk of different substances could be compared for priority setting. [Pg.289]

Pollutants — Handbooks, manuals, etc. 2. Hazardous substances — Risk assessment — Handbooks, manuals, etc. 3. Environmental chemistry — Handbooks, manuals, etc. 4. Environmental risk assessment — Handbooks, manuals, etc. I. Title. [Pg.7]

Under both national and international agreements, the process of quantitatively predicting the probability of an adverse response in ecosystem health due to exposure to one or more pollutants is collectively known as Environmental Risk Assessment, ERA (US EPA, 1992). [Pg.75]

In accordance with this definition, an environmental risk assessment process is used especially in cases when the probability component arises during the calculation of various parameters which can be due to many reasons uncertainty of input information uncertainties in applying an algorithm due to lack of knowledge, insufficient knowledge and/or simplification of input information uncertainties in the defined geographic boundaries of pollutant influence uncertainties in both computer calculations and management operations based on these calculations. [Pg.75]

Thus, from the viewpoint of environmental risk assessment (critical loads) the most important exposure pathways are nitrate leaching and denitrification, which are both very sensitive to anthropogenic pollution. These links of biogeochemical nitrogen cycle should be firstly quantitatively parameterized to assessing environmental risk. [Pg.141]

Many quantitative aspects of exposure pathways and their relevant application during environmental risk assessment depend on regional biogeochemical peculiarities and should be undoubtedly considered on the regional scale. Accordingly this part includes some characteristic examples and case studies from local up to regional and continental dimensions. We discuss the importance of the trans-boundary of pollutant exposure as well as the application of critical load methodology for risk estimates. [Pg.260]

ENVIRONMENTAL RISK ASSESSMENT OF AIR POLLUTION INDUCED DISEASES... [Pg.283]

CONCEPTUAL MODEL FOR THE ENVIRONMENTAL RISK ASSESSMENT OF POLLUTANTS ENTERING THE CASPIAN SEA... [Pg.310]

Thus the consideration of kinetics of POP sorption by particulate soil organic matter appreciably changes the pollutant vertical distribution, particularly during the clearance period, which increases this period substantially. Accordingly, this is of great importance to environmental risk assessment of POPs exposure to living organisms. [Pg.400]

Bashkin, V. N. (1999). Environmental risk assessment under calculation of critical loads of pollutants at ecosystems. Geography and Natural Resources, 1, 35-39... [Pg.424]

In conclusion, the authors of the cited studies all agree that further research into environmental risk assessment of hospital effluents, incorporating different types of substances used in care and diagnostic activities, as well as cleaning operations (pharmaceuticals, detergents, disinfectants, heavy metals, macropollutants), is vital. Moreover, further studies need to be focussed on evaluating the risk posed by pollutant mixtures, and work is needed to validate the predictive models proposed thus far [19, 49], to evaluate chronic toxicity due to PhCs and then-mixtures and to provide experimental data pertaining to specific case studies. [Pg.162]

Scholz S, Fischer S, Giindel U et al (2008) The zebrafish embryo model in environmental risk assessment—applications beyond acute toxicity testing. Environ Sci Pollut Res Int 15(5) 394 04... [Pg.341]

In this chapter we provide an overview of the chemistry of the lower and upper atmospheres. In Chapter 2, we illustrate how this chemistry plays a critical role in the concept of an integrated atmospheric chemistry system —a loop that starts with emissions (anthropogenic and natural) and ultimately closes with scientific health and environmental risk assessments and associated risk management decisions for the control of air pollutants. [Pg.1]

Jamil K. 2001. Bioindicators and biomarkers of environmental pollution and risk assessment. Plymouth (UK) Science Publishers, 204 p. [Pg.342]

A hazard is anything that will produce an adverse effect on human health and the environment. In environmental risk assessment, the hazard component generally refers to toxicity. Exposure is the quantitative or qualitative assessment of contact to the skin or orifices of the body by a chemical. Traditional pollution prevention techniques focus on reducing waste as much as possible however, risk assessment methods used in pollution prevention can help quantify the degree of environmental impact for individual chemicals. This approach provides a powerful tool that enables engineers to better design processes and products by focusing on the most beneficial methods to minimize all aspects of risk. [Pg.211]

Scholz S., Fisher S., Gundel U., Kuster E., Luckenbach T. Voelker D. (2008) The zebra fish embryo model in environmental risk assessment - application beyond acute toxicity testing. Environmental Science and Pollution Research International 15 394-404. [Pg.118]

See also Ecotoxicology Environmental Toxicology Pollution, Water Risk Assessment, Ecological. [Pg.932]

See also Analytical Toxicology Biomarkers, Environmental Ecotoxicology Effluent Biomonitoring Environmental Toxicology Microtox Photochemical Oxidants Pollution, Water Risk Assessment, Ecological. [Pg.2630]


See other pages where Pollution environmental risk assessment is mentioned: [Pg.24]    [Pg.18]    [Pg.18]    [Pg.69]    [Pg.78]    [Pg.157]    [Pg.244]    [Pg.294]    [Pg.315]    [Pg.319]    [Pg.322]    [Pg.323]    [Pg.327]    [Pg.263]    [Pg.1]    [Pg.143]    [Pg.214]    [Pg.214]    [Pg.344]    [Pg.449]    [Pg.170]    [Pg.112]    [Pg.166]    [Pg.85]    [Pg.341]   
See also in sourсe #XX -- [ Pg.691 ]




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