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The Impact of Pesticides - Academy Publish

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5,000 trials based on the probabilities distribution <strong>of</strong> each variable. As previouslystated, based on accidental ingestion dose and dermal contact dose, the simultaneousrisk was calculated in both contact ways for each substance (aggregate risk) for theNon Cancer effects and for the Cancer ones. <strong>The</strong> process <strong>of</strong> addition is conductediteration by iteration, so the results are a new distribution <strong>of</strong> values, for whichdescriptive statistics are obtained for later analysis.Biota Health Risk EstimationIt was previously stated that the risk to biota is estimated based on the ratioPEC/PNEC for selected ecosystem organisms. <strong>The</strong> PEC value used is thedistribution <strong>of</strong> probability <strong>of</strong> the concentrations <strong>of</strong> each pesticide, as performed forthe calculation <strong>of</strong> Human Health Risk. <strong>The</strong> Health Risk Biota result is a distribution<strong>of</strong> values obtained by adding the PEC/PNEC ratios for the two obtained biologicalgroups, iteration by iteration, by the application <strong>of</strong> Monte Carlo. From these, it wasalso obtained descriptive statistics to conduct analysis <strong>of</strong> the results.Interpretation <strong>of</strong> the Results <strong>of</strong> the DelAzulPestRisk Model<strong>The</strong> results <strong>of</strong>fered by the model cannot be considered a formal measurement <strong>of</strong> riskbut an indication <strong>of</strong> it, since the model includes variables that are risk measures(human and biological) with others that are not (the half-life and thebioaccumulation potential). <strong>The</strong> risk values are dimensionless while neither life northe bioaccumulation potential are, so the integration <strong>of</strong> these terms ignoring theunits <strong>of</strong> the latter is a methodological decision that makes the model not a " risk"model but a "risk-based" one.Statistical Analysis<strong>The</strong> statistical analysis (obtaining descriptive statistics <strong>of</strong> the probabilitydistributions following the Monte Carlo application or determining the best fitmodel <strong>of</strong> probability distribution) was performed using Crystal Ball(Decisioneering, 2007), as well as the sensitivity analysis. This calculates sensitivitybased on the rank correlation coefficients between every parameter <strong>of</strong> the model andthe model results while the simulation is running (Decisioneering, 2007).RESULTS<strong>The</strong> risk to human health analysis results show that no substance by itself is capable<strong>of</strong> producing health effects to the population, not even considering the carcinogeniceffects or the non carcinogenic ones, which had already been evidenced by Peluso etal. (2011b). However, in the DelAzulPestRisk model, the risks for carcinogeniceffects are finally estimated as a proportion <strong>of</strong> the value used as reference (10E -05 ),so the risk threshold value for each substance is 1 for each type <strong>of</strong> effect. If thesubstance has both types <strong>of</strong> effects (as it happens with the isomers <strong>of</strong> HCH, Aldrin,Chlordane and Heptachlor), the risk threshold value to health in theDelAzulPestRisk model is all the same 1. From the results presented in Table 5, itcan be seen that the substance that creates the greatest risk to human health is<strong>Academy</strong><strong>Publish</strong>.org - <strong>The</strong> <strong>Impact</strong> <strong>of</strong> <strong>Pesticides</strong>253

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