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                             sensible view, considering the  fact that nothing is wholly safe per se. In  fact,
                             whereas large amounts of toxic substances may be of major concern, simply
                             detecting a hazardous chemical in the environment should not necessarily be a
                             cause for alarm. The intrinsic knowledge of the physical–chemical properties of
                             pollutants, biodegradability, potential of bioaccumulation or potential effects of
                             the chemical substances is necessary for the  evaluation of environmental risk.
                             Moreover, it is necessary to carry out a detailed evaluation of the emission sources,
                             as well as the fate, transport and distribution in the different media. Due to all
                             this, the analysis of environmental samples in the laboratory and the application
                             of mathematical models are vital (EC, 1996).



                             4.3  FRAMEWORK OF ENVIRONMENTAL RISK
                                 ASSESSMENT

                             ERA is a formal mathematical tool used to evaluate potential hazards introduced by
                             pollutant emissions in human health and the environment.  This risk assessment
                             process entails a sequence of actions outlined below:

                                1. Hazard identification: identification of the adverse effect that a substance
                                   has an inherent capacity to cause
                                2. Exposure assessment: estimation of the concentrations/doses to which
                                   human populations (i.e.,  workers, consumers and individuals  exposed
                                   indirectly via the environment) or environmental compartments (aquatic
                                   environment, terrestrial environment and air) are or may be exposed
                                3. Dose–response assessment: estimation of the relationship between dose,
                                   or level of exposure to a substance, and the incidence and severity of an
                                   effect
                                4. Risk characterization:  estimation of the incidence and severity of the
                                   adverse effects likely to occur in a human population or environmental
                                   compartment due to actual or predicted exposure to a substance, i.e., the
                                   quantification of that likelihood


                                Figure 4.1 shows a framework for human and ecological ERA. The EU has
                             provided a technical guidance document on ERA in support of Commission
                             Directive 93/67/EEC on Risk Assessment for New Notified Substances and the
                             Commission Regulation (EC) 1488/94 on Risk  Assessment for Existing Sub-
                             stances (EC, 1996).  The U.S. Environmental Protection Agency has produced
                             different risk assessment guidelines: Guidelines for Ecological Risk Assessment
                             (EPA/630/R-95/002F. FR 63(93) 26846–26924), the Guideline for Exposure
                             Assessment (EPA/600Z-92/001. FR 57: 22888–22938) and the Proposed Guide-
                             line for Carcinogenic Risk  Assessment (EPA/600/P-92/003C. FR 61(79)
                             17960–18011).




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