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The Impact of Pesticides - Academy Publish

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must be considered, since effective activities occurs in an open air (Colosio et al.,2011). For this reason, Colosio et al. (2011) developed an integrated user-friendlytool for risk assessment and management in agriculture, in which the computationalmodelling was added to biological, and environmental monitoring.Most <strong>of</strong> the population may be exposed to carbamates through dietary (e.g.consumption <strong>of</strong> treated fruits, vegetables and contaminated water) (Lu et al., 2010).Hazard characterization involves comparing the pesticide exposure concentrationwith the ADI or the ARfD (the estimate <strong>of</strong> the amount <strong>of</strong> a substance in food thatcan be ingested over a short period <strong>of</strong> time, usually during one meal or one day,without appreciable health risk to the consumer) (WHO 1997; Keikotlhaile et al.,2011). In exposure assessment, the potential intake or consumption <strong>of</strong> pesticideresidues is divided by the body weight and compared to ADI or ARfD (Exposure =(Concentration <strong>of</strong> pesticide residue x Food consumed)/ body weight) (Keikotlhaileet al., 2011).Long-term averaged daily intake <strong>of</strong> contaminants such as pesticide residues in foodmay be estimated using NORMTOX (Ragas and Huijbregts, 1998; Ragas et al.,2009). Schulte-Oehlmann et al. (2011) reviewed the monitoring data over a 10-yearperiod and revealed that although the percentage <strong>of</strong> foodstuff without detectablepesticide residues in Germany has continuously decreased from 64 to 51.5%, forcarbaryl ARfDs were exceeded substantially. Among other pesticides, carbamateswere also rated as endocrine-active factors (Schulte-Oehlmann et al., 2011). In view<strong>of</strong> the probable health risk <strong>of</strong> a wide range <strong>of</strong> pesticides, a new EU regulation isbeing prepared, including the test criteria for these chemicals to be finalized by2013.Humans are sequentially or simultaneously exposed to a wide range <strong>of</strong> pollutants,instead to only one. Due to the main limitations and complex approach to certainlyevaluate the health effects <strong>of</strong> complex mixtures few studies were undertaken toexplore this complexity. Recently, Ragas and co-workers (2011) have investigatedthe cumulative health risk effects <strong>of</strong> a wide range <strong>of</strong> stressors, including pesticides,on different target groups (young children, working adults and elderly). This surveywas based on the time spent in different microenvironments, the outdoor movement,and food consumption patterns. Different scenarios for assessing mixture effects fora better understanding <strong>of</strong> mechanism <strong>of</strong> action, and interactions (antagonistic orsynergistic) were considered. In conclusion, this review underlines the need forperson-oriented exposure models that can simulate the cumulative exposure history<strong>of</strong> individuals based on realistic activity and consumption patterns; in addition, abetter mechanistic understanding <strong>of</strong> the effects <strong>of</strong> cumulative stressors is relevant.CONCLUSIONS<strong>The</strong> increase <strong>of</strong> carbamate applications makes the implications for theenvironmental and biomedical research communities a significant endeavor. Diet,and principally fruit and fruit juices, is the major carbamates source for nonoccupationallyexposed population. <strong>The</strong> dietary acute intake <strong>of</strong> some carbamates(AChE inhibitors) as previously evaluated by the FAO/WHO Joint Meeting on<strong>Academy</strong><strong>Publish</strong>.org - <strong>The</strong> <strong>Impact</strong> <strong>of</strong> <strong>Pesticides</strong>30

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