title: Community air monitoring for pesticides. Part 3: using health-based screening levels to evaluate results collected for a year.
abstract: The CA Department of Pesticide Regulation (CDPR) and the CA Air Resources Board monitored 40 pesticides, including five degradation products, in Parlier, CA, to determine if its residents were exposed to any of these pesticides and, if so, in what amounts. They included 1,3-dichloropropene, acrolein, arsenic, azinphos-methyl, carbon disulfide, chlorpyrifos and its degradation product, chlorthalonil, copper, cypermethrin, diazinon and its degradation product, dichlorvos, dicofol, dimethoate and its degradation product, diuron, endosulfan and its degradation product, S-ethyl dipropylcarbamothioate (EPTC), formaldehyde, malathion and its degradation product, methyl isothiocyanate (MITC), methyl bromide, metolachlor, molinate, norflurazon, oryzalin, oxyfluorfen, permethrin, phosmet, propanil, propargite, simazine, SSS-tributylphosphorotrithioate, sulfur, thiobencarb, trifluralin, and xylene. Monitoring was conducted 3 days per week for a year. Twenty-three pesticides and degradation products were detected. Acrolein, arsenic, carbon disulfide, chlorpyrifos, copper, formaldehyde, methyl bromide, MITC, and sulfur were detected in more than half the samples. Since no regulatory ambient air standards exist for these pesticides, CDPR developed advisory, health-based non-cancer screening levels (SLs) to assess acute, subchronic, and chronic exposures. For carcinogenic pesticides, CDPR assessed risk using cancer potency values. Amongst non-carcinogenic agricultural use pesticides, only diazinon exceeded its SL. For carcinogens, 1,3-dichloropropene concentrations exceeded its cancer potency value. Based on these findings, CDPR has undertaken a more comprehensive evaluation of 1,3-dichloropropene, diazinon, and the closely related chlorpyrifos that was frequently detected. Four chemicals-acrolein, arsenic, carbon disulfide, and formaldehyde-sometimes used as pesticides were detected, although no pesticidal use was reported in the area during this study. Their presence was most likely due to vehicular or industrial emissions.
authors.affiliation: Environmental Monitoring Branch, Department of Pesticide Regulation, CA Environmental Protection Agency, P.O. Box 4015, Sacramento, CA, 95812, USA, pwofford@cdpr.ca.gov.
authors.forename: Pamela
authors.initials: P
authors.lastname: Wofford
authors.forename: Randy
authors.initials: R
authors.lastname: Segawa
authors.forename: Jay
authors.initials: J
authors.lastname: Schreider
authors.forename: Veda
authors.initials: V
authors.lastname: Federighi
authors.forename: Rosemary
authors.initials: R
authors.lastname: Neal
authors.forename: Madeline
authors.initials: M
authors.lastname: Brattesani
mesh_terms: D000383:Agriculture; D000393:Air Pollutants / Q000032:analysis*; D000397:Air Pollution / Q000032:analysis / Q000331:legislation & jurisprudence / Q000706:statistics & numerical data; D002140:California / Q000453:epidemiology; D003256:Community Participation; D004781:Environmental Exposure / Q000032:analysis* / Q000706:statistics & numerical data; D004784:Environmental Monitoring / Q000379:methods; D006304:Health Status; D006801:Humans; D009369:Neoplasms / Q000453:epidemiology; D010575:Pesticides / Q000032:analysis*; D012111:Residence Characteristics; D018570:Risk Assessment
chemical_list: D000393:Air Pollutants; D010575:Pesticides