Assessing breeding potential of peregrine falcons based on chlorinated hydrocarbon concentrations in prey.
Peregrine falcons (Falco peregrinus) now breed successfully in most areas of North America from which they were previously extirpated. The loss during the mid-part of the last century of many of the world's peregrine populations was largely a consequence of impaired reproduction caused by the effects of DDE on eggshell quality and embryo hatchability. Population recovery has been attributed to re-introduction efforts, coupled with regulatory restrictions on the use of organochlorine pesticides. Peregrines have not returned to breed in some areas, such as the Okanagan Valley of British Columbia. That region has been extensively planted in fruit orchards which were treated annually with DDT during the early 1950s to the 1970s. Ongoing contamination of avian species, including potential peregrine prey, inhabiting orchards has been documented. In response to an initiative to release peregrines around the city of Kelowna in the Okanagan Valley, we collected potential peregrine prey species and analyzed whole bodies for chlorinated hydrocarbon residues. We used a simple bioaccumulation model to predict concentrations of DDE in peregrine eggs using concentrations in prey and estimates of dietary makeup as input. Peregrines would be expected to breed successfully only if they fed on a diet primarily of doves. Feeding on as little as 10% of other species such as starlings, robins, gulls and magpies would produce DDE concentrations in peregrine eggs greater than the threshold of 15 mg/kg. We also estimated the critical concentration of DDE in total prey to be about 0.5 mg/kg, one half of the previous most conservative criterion for peregrine prey. Concentrations of dieldrin and PCBs in peregrine prey are less than suggested critical levels.
Elliott
J E
JE
Canadian Wildlife Service, Pacific Wildlife Research Centre, 5421 Robertson Rd., RR # 1, Delta, British Columbia, V4K 3N2, Canada. john.elliott@ec.gc.ca
Miller
M J
MJ
Wilson
L K
LK
D000818:Animals; D046091:Charadriiformes; D010856:Columbidae; D003634:DDT / Q000032:analysis; D003633:Dichlorodiphenyl Dichloroethylene / Q000032:analysis; D004531:Eggs / Q000032:analysis; D004781:Environmental Exposure / Q000009:adverse effects; D004784:Environmental Monitoring / Q000379:methods; D004785:Environmental Pollutants / Q000032:analysis*; D046093:Falconiformes / Q000502:physiology*; D006843:Hydrocarbons, Chlorinated / Q000032:analysis*; D007306:Insecticides / Q000032:analysis; D010575:Pesticides / Q000032:analysis; D011235:Predatory Behavior; D012098:Reproduction / Q000187:drug effects* / Q000502:physiology; D018570:Risk Assessment / Q000379:methods; D020308:Songbirds
D004785:Environmental Pollutants; D006843:Hydrocarbons, Chlorinated; D007306:Insecticides; D010575:Pesticides; D003633:Dichlorodiphenyl Dichloroethylene; D003634:DDT