Methodology for Exposure and Risk Assessment in Complex Environmental Pollution Situations
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Citations
Exposure Assessment to Heavy Metals in the Environment: Measures to Eliminate or Reduce the Exposure to Critical Receptors
References
MinUrar - Minas de Urânio e seus resíduos: efeitos na saúde da população - Relatório científico I
Modeling the transport and fate of contaminants in the environment: soil, water and air
Related Papers (1)
Frequently Asked Questions (9)
Q2. What were the parameters needed to describe the exposure scenario?
Radionuclide and chemical concentration in soil, air and groundwater, were needed along with parameters describing the exposure scenario.
Q3. How many ha of contaminated soil are there?
The contaminated site represents an area of 13,3 ha and until a very recent past radionuclides and chemicals have been released to the air, soil, surface water and indirectly to groundwater as a result of routine operations, accidents and waste disposal practices.
Q4. What is the current plan for a tailings reclamation scheme?
a rehabilitation plan based on an in-situ reclamation scheme to promote the confinement of the tailings materials is under implementation as well as a wastewater treatment system implemented in the mining area (Nero et al., 2005).
Q5. How many people are affected by contaminated leafy vegetables?
The total incremental cancer risk incurred by the ingestion of contaminated soil, water, leafy vegetables and milk is 1,81 x 10 -3 , which means an excess risk of one in one thousand mainly due to leafy vegetable ingestion and water ingestion.
Q6. What is the definition of a release assessment?
A release assessment involves the identification of the risk potential source to introduce hazardous agents into the environment.
Q7. What are the main sources of uncertainty in the ERA?
Uncertainty can arise from several potential sources (Calewaert, 2006): Uncertainty inherent to methods used in each of the ERA steps: choice ofmodel, assumptions made in used models, uncertainties related to the model structure itself as the lack of confidence that the mathematical model is an adequate representation of the assessment problem; Uncertainty related to the collected data and parameters: gaps inhistoric/recent data, use of data from other situations and extrapolations to fill out gaps, variability of a model parameter from its true heterogeneity over space and time, uncertainty of a model parameter resulting from the lack of information or knowledge about its true value; Uncertainty of the analyst: interpretation of ambiguous or incompleteinformation, human error, uncertainty of how an assessor translates a real or forecasted situation in a given model.
Q8. What is the hazard quotient for beryllium exposure?
The resulting hazard quotient to quantify the noncarcinogenic health effects incurred by beryllium inhalation is HQ = 0,05 which is inferior to one; the exposure to beryllium in this scenario does not pose any risk.
Q9. What is the effect of the public perception of risk?
On its turn, the public perception of risk depends on the economic, social, legal and political context in which the affected and/or concerned population lives (Fairman et al., 1998).