1996
DOI: 10.2307/3802231
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Monitoring Great Horned Owls for Pesticide Exposure in Southcentral Iowa

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Cited by 10 publications
(7 citation statements)
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“…The nocturnal lifestyle does not seem to be a criterion for a high level of ChE activity because Buck et al (1996) found 2.4-4.8 times lower activities in great horned owl (Bubo virginianus) than in nocturnal species in our study. However, this American species is larger and shows a greater AChE:BChE ratio (near one) than the Strigidae species of the present study.…”
Section: Discussionmentioning
confidence: 59%
“…The nocturnal lifestyle does not seem to be a criterion for a high level of ChE activity because Buck et al (1996) found 2.4-4.8 times lower activities in great horned owl (Bubo virginianus) than in nocturnal species in our study. However, this American species is larger and shows a greater AChE:BChE ratio (near one) than the Strigidae species of the present study.…”
Section: Discussionmentioning
confidence: 59%
“…There are several possible explanations for this apparent discrepancy between measured pathways of exposure (air and diet) and the biomarker (TCPy) of exposure. One possibility is that dermal and/or soil ingestion plays a far greater role in exposures than was predicted by the modeling exercise of Buck et al (1996). However, this seems highly unlikely, since the exposure assumptions were somewhat conservative, and it is unlikely that the estimates would be off by several orders of magnitude (which would be required for these pathways to account for >90% of the "excess" TCPy found in urine).…”
Section: Vc5 Limitations Of Use Of Tcpy As a Biomarker For Chlor-mentioning
confidence: 99%
“…When adjusted for age and body weight, partial aggregate daily intake rates were 0.012 µg/kg-day, of which approximately 94% was derived from diet and 6% was from inhalation exposures. Earlier modeling exercises that incorporated surface loading and hand wash data along with numerous assumptions about exposures via the dermal and inhalation pathways (Buck et al, 1996) yielded an estimate of a median exposure of 0.09 µg/kg-day (∼8 times greater than the measured exposures of Clayton et al, 2003), from which 81% was estimated to be due to inhalation exposure, and 19% from diet (Buck et al, 1996). The modeling exercise of Buck et al suggested that soil ingestion and the dermal pathways were relatively insignificant pathways for exposure (each contributing less than 0.1% of total estimated exposure).…”
Section: Vc5 Limitations Of Use Of Tcpy As a Biomarker For Chlor-mentioning
confidence: 99%
“…Though one of the birds, an American robin, contained no chlorpyrifos, there were no further analyses for other organophosphorus insecticides. As documented in studies with great-horned owls in similar Iowa habitat (Buck et al 1996) and raptor species in California's Central Valley (Gallagher et al 1994), chlorpyrifos treatments often coincide with applications of other anti-AChE pesticides in adjacent farmland where wildlife can travel, dividing their time over multiple exposure scenarios. Comparisons of chlorpyrifos-treated fields are made with nontreated reference sites and the number of mortalities on reference sites establishes the anticipated background casualty frequency for the treatment sites.…”
Section: Terrestrial Risk Assessment For Chlorpyrifos In Corn Agroecomentioning
confidence: 95%
“…A study using radio-tagged great horned owls, which consume small mammals that could contain insecticide residues, demonstrated anti-AChE exposure, but no effects, following insecticidal treatment of corn fields (Buck et al 1996). Seven owls were monitored in 1988 and 15 in 1989, both before and after treatment of corn fields in south central Iowa with terbufos granules (as Counter ® 15G Insecticide) or chlorpyrifos granules (as Lorsban ® 15G).…”
Section: Terrestrial Risk Assessment For Chlorpyrifos In Corn Agroecomentioning
confidence: 99%