ADI and ARfD defined by FAO/WHO Joint Meeting on Pesticide
Residues (JMPR) were used to evaluate the pesticide residue levels
found in the Bolivian tomatoes. ADI and ARfD values are presented
in Table 1and are mainly retrieved from British Crop Protection
Council (2014). As surveillance data of local Bolivian tomato consumption
was not available, the values estimated by WHO were
used (EFSA/FAO/WHO, 2011). For chronic intake of tomatoes an average
of 25 g of tomato per person per day is estimated for most
South American countries, including Bolivia. The adult body weight
is estimated to be 52.2 kg, while for children it is 18.9 kg. For chronic
risk assessment 25 g of tomato/day (app. 1/4 tomato) is the suggested
intake value, while for acute risk one large portion of either
385 g of tomatoes for an adult or 215 g of tomatoes for a child is
the suggested intake value (EFSA/FAO/WHO, 2011). For pesticides
with the same mode of action, dose addition was assumed (Boobis
et al., 2008). Thus the Hazard Index was used as described in
Eq. (2) for organochlorines and organophosphates separately.
ADI and ARfD defined by FAO/WHO Joint Meeting on PesticideResidues (JMPR) were used to evaluate the pesticide residue levelsfound in the Bolivian tomatoes. ADI and ARfD values are presentedin Table 1and are mainly retrieved from British Crop ProtectionCouncil (2014). As surveillance data of local Bolivian tomato consumptionwas not available, the values estimated by WHO wereused (EFSA/FAO/WHO, 2011). For chronic intake of tomatoes an averageof 25 g of tomato per person per day is estimated for mostSouth American countries, including Bolivia. The adult body weightis estimated to be 52.2 kg, while for children it is 18.9 kg. For chronicrisk assessment 25 g of tomato/day (app. 1/4 tomato) is the suggestedintake value, while for acute risk one large portion of either385 g of tomatoes for an adult or 215 g of tomatoes for a child isthe suggested intake value (EFSA/FAO/WHO, 2011). For pesticideswith the same mode of action, dose addition was assumed (Boobiset al., 2008). Thus the Hazard Index was used as described inEq. (2) for organochlorines and organophosphates separately.
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