RESUMO
A rapid liquid chromatography tandem mass spectrometry (LC-MS/MS) method has been developed for determination of levels of the organophosphorus (OP) pesticides chlorpyrifos (CPF), azinphos methyl (AZM), and their oxygen analogs chlorpyrifos-oxon (CPF-O) and azinphos methyl-oxon (AZM-O) on common active air sampling matrices. XAD-2 resin and polyurethane foam (PUF) matrices were extracted with acetonitrile containing stable-isotope labeled internal standards (ISTD). Analysis was accomplished in Multiple Reaction Monitoring (MRM) mode, and analytes in unknown samples were identified by retention time (±0.1 min) and qualifier ratio (±30% absolute) as compared to the mean of calibrants. For all compounds, calibration linearity correlation coefficients were ≥0.996. Limits of detection (LOD) ranged from 0.15-1.1 ng/sample for CPF, CPF-O, AZM, and AZM-O on active sampling matrices. Spiked fortification recoveries were 78-113% from XAD-2 active air sampling tubes and 71-108% from PUF active air sampling tubes. Storage stability tests also yielded recoveries ranging from 74-94% after time periods ranging from 2-10 months. The results demonstrate that LC-MS/MS is a sensitive method for determining these compounds from two different matrices at the low concentrations that can result from spray drift and long range transport in non-target areas following agricultural applications. In an inter-laboratory comparison, the limit of quantification (LOQ) for LC-MS/MS was 100 times lower than a typical gas chromatography-mass spectrometry (GC-MS) method.
Assuntos
Poluentes Atmosféricos/análise , Cromatografia Líquida/métodos , Monitoramento Ambiental/métodos , Organotiofosfatos/análise , Praguicidas/análise , Espectrometria de Massas em Tandem/métodos , Limite de Detecção , Poliestirenos/química , Poliuretanos/química , Fatores de TempoRESUMO
A cross-sectional study with repeated sample collection in multiple days was conducted to assess diazinon exposures. Saliva and limited blood samples were collected from 10 banana plantation workers involved with diazinon application and their children aged 2-12 years living in Chinandega, Nicaragua. Diazinon concentration-time profiles in saliva varied between two plantations, which reflects the differences of work practices in each plantation. Salivary concentrations of diazinon measured in Plantation 1 applicators continued to increase 2 days after self-reported diazinon application, suggesting an ongoing exposure among these workers. However, salivary diazinon concentrations measured in Plantation 2 applicators were peaked 12 h prior to the first application, and then decreased 36 h post the first application. Diazinon concentrations in saliva were significantly correlated with the time-matched plasma samples collected from the same workers, which is in agreement with the previous published data from animal models. Children's exposure to diazinon through take-home pathway does not exist, as evident by the majority of nondetected saliva samples, and this finding was confirmed by the results from the urine samples. Severe dehydration was observed in many plantation workers and their children, resulting in the loss of some saliva samples, which no doubt have impaired the overall quality of the study results. Regardless, this article has demonstrated that saliva can be used to assess exposures to diazinon in pesticide applicators and children.
Assuntos
Agricultura , Diazinon/toxicidade , Monitoramento Ambiental , Inseticidas/toxicidade , Exposição Ocupacional , Saliva/química , Adulto , Criança , Pré-Escolar , Estudos Transversais , Diazinon/análise , Diazinon/sangue , Humanos , Inseticidas/análise , Inseticidas/sangue , Nicarágua , Reprodutibilidade dos TestesRESUMO
Organophosphorus pesticides are some of the most widely used insecticides in the US, and spray drift may result in human exposures. We investigate sampling methodologies using the polyurethane foam passive air sampling device to measure cumulative monthly airborne concentrations of OP pesticides chlorpyrifos, azinphos-methyl, and oxygen analogs. Passive sampling rates (m(3)d(-1)) were determined using calculations using chemical properties, loss of depuration compounds, and calibration with side-by-side active air sampling in a dynamic laboratory exposure chamber and in the field. The effects of temperature, relative humidity, and wind velocity on outdoor sampling rates were examined at 23 sites in Yakima Valley, Washington. Indoor sampling rates were significantly lower than outdoors. Outdoor rates significantly increased with average wind velocity, with high rates (>4m(3)d(-1)) observed above 8ms(-1). In exposure chamber studies, very little oxygen analog was observed on the PUF-PAS, yet substantial amounts chlorpyrifos-oxon and azinphos methyl oxon were measured in outdoor samples. PUF-PAS is a practical and useful alternative to AAS because it results in little artificial transformation to the oxygen analog during sampling, it provides cumulative exposure estimates, and the measured sampling rates were comparable to rates for other SVOCs. It is ideal for community based participatory research due to low subject burden and simple deployment in remote areas.
Assuntos
Poluentes Atmosféricos/análise , Monitoramento Ambiental/instrumentação , Praguicidas/análise , Agricultura , Azinfos-Metil/análise , Clorpirifos/análogos & derivados , Clorpirifos/análise , Cromatografia Líquida de Alta Pressão , Poliuretanos/química , Espectrometria de Massas em Tandem , TemperaturaRESUMO
Side-by-side active air sampling for the organophosphorus (OP) pesticide, chlorpyrifos (CPF) and its oxygen analog, chlorpyrifos-oxon (CPF-O) was conducted with two recommended air sampling matrices: OSHA Versatile Sampling (OVS) tubes with XAD-2 resin, polyurethane foam (PUF) tubes, and passive PUF deposition disks. The study compared the proportion of artificially transformed CPF-O in the laboratory and in the field during a tree fruit application in Washington State. Lab results demonstrated that the NIOSH-recommended OVS tubes artificially transformed up to 32% of CPF to CPF-O during the sampling process, whereas PUF tubes had little to no artificial transformation (⩽0.1%). In the field, the proportion of CPF-O in the sample was significantly higher on OVS tubes than on PUF tubes (p<0.001), confirming that OVS tubes were converting a significant portion of CPF to CPF-O. In addition, PUF tubes reported measurable levels CPF-O in the field even when no artificial transformation was expected. We conclude that the PUF matrix is the superior sampling medium for OP oxygen analogs when compared to XAD-two resin. Community-located PUF tube samples 24h post-application had considerably higher levels CPF-O (16-21ngm(-3)) than near field samples during application (2-14ngm(-3)), suggesting that the oxygen analog is volatile and formed during atmospheric transport. It is recommended that worker and community risk assessments begin to take into consideration the presence of the more toxic oxygen analogs when measuring for OP pesticide mixtures.