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Definition and Characterization of the Sources of DDT Contamination Currently Impacting White-faced Ibis Populations

 

The white-faced ibis (Plegadis chihi) is a long-legged wading bird that feeds primarily on invertebrates in wetlands and irrigated croplands.   It is a highly social colonial nester and often forages in large aggregations.  Due to restricted nesting habitat and potential vulnerability to pesticides, the species is listed by the U.S. Fish and Wildlife Service as a migratory non-game bird of management concern.

 

Dr. Charles Henny (U.S. Geological Survey; USGS) has documented continued troubling levels of DDE in a large segment of the white-faced ibis population nesting at Carson Lake in western Nevada.  Of twenty eggs collected in 1996, 45% contained >4 ppm DDE, and eggshells averaged 18.3% thinner than normal.  This represented no improvement from DDE levels documented in 1985-86, which is contrary to patterns shown for most other avian species in the USA.  Analyses of upper digestive tract contents in 18 Carson Lake ibis revealed no organochlorine insecticides; the conclusion is that DDE/DDT contamination is not occurring on the Nevada breeding grounds.  Identification of contaminant sources is highly desirable because it is likely that different regional cohorts of ibis and other wildlife species are frequenting those same areas.

 

Accordingly the Raptor Research Center, along with Earthspan, the Center for Conservation Research and Technology, USGS, U.S. Fish and Wildlife Service, and Nevada Division of Wildlife conducted a pilot study in 1997 to determine whether white-faced ibis could be tracked via satellite-received telemetry.  This was part of another study funded by the Department of Defense (DoD) Legacy Resource Management Program. Two ibis were successfully tracked.  This proof-of-concept convinced Legacy to fund an investigation into source(s) of DDE contamination in ibis, which are known to frequent various DoD lands throughout the west.

 

In early May 2000, with our cooperators, we captured 15 white-faced ibis from the vicinity of a nesting colony at Carson Lake, NV.  Ten birds were marked with ~20g satellite-received Platform Transmitter Terminals (PTTs).  Blood samples (~1ml) were taken from the brachiocephalic vein.  PTT transmissions were received by Argos satellites and location estimates relayed to researchers.  To conserve battery energy to obtain most locations after the birds left the breeding area, we programmed the units in an unconventional and untested manner.  During the breeding season, the PTTs transmitted only six hours every two weeks, while we hoped to maintain battery integrity with minimal loss of capacity.  The PTTs were programmed to begin transmitting eight hours every three days in October, near the time our subjects should be departing the breeding ground.  The plan was a success, and seven PTTs produced high quality locations for the detailed information we needed to identify potential sources of DDT. An eighth PTT provided good data, but the ibis apparently died in western Colorado while still on migration.

Seven of our ten subjects had detectable blood DDE levels; three had high levels (>0.25 ppm), and four others low levels (<0.15 ppm). Winter fieldwork began in January 2001. Using the most accurate Argos location data to guide us, we visited the wintering sites of our sentinel ibis from Carson Lake and collected samples of invertebrates where ibis were feeding.  Such sampling may reveal significant sources of contaminants posing a threat to numerous species.  Information revealed by the technology applied on this project prompted, in another study, mitigation of organophosphate pesticide poisoning of thousands of Swainson’s hawks in Argentina.  We made necessary collections from four such sites in California’s Central Valley between the Bakersfield and Yuba City areas, and documented associated birdlife, habitat characteristics, and farming practice in those areas.  We had excellent cooperation from landowners and managers.  A colleague collected samples and similar information where another individual apparently died on its wintering area in Jalisco State, Mexico. Two other individuals wintering in Mexico (Colorado River Delta area) had high DDE blood levels, but collection permits were not forthcoming in time to visit the area during the wintering period. Analyses of invertebrate samples revealed elevated DDE levels in some earthworm samples, so further collections at wintering sites focused on earthworms.

 

In late May 2003, with Legacy and Earthspan’s support, we blood sampled and outfitted another ten ibis at Carson Lake with PTTs. All ten had detectable blood DDE levels, and they were generally higher than those recorded for 2000 subjects. Five of the ten had high levels (>0.25 ppm), and three of those were higher (range 0.744 - 0.99 ppm) than any recorded in 2000.  Two had medium levels (0.15 – 0.24 ppm), and three had low levels (<0.15 ppm).  Satellite locations defined the wintering areas of five subjects, three in Mexico and two in California’s Central Valley.

 

During February 2004 earthworm collections were made in Mexico at the three current wintering sites and at the two 2001 wintering sites that could not be visited previously. Three of those sampling sites were in the Colorado River Delta area, and the blood DDE levels of the ibis associated with those sites were among our highest recorded during the study. We also made earthworm collections at the two current California wintering sites and at three 2001 sites where we had previously sampled different invertebrates.  Analysis found high DDE levels only among earthworms collected at the three Mexicali Valley wintering sites, identifying that locale as a significant source of organochlorine contaminants. 

We wish to acknowledge the participation and contributions of:

 

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  This page was last reviewed on 20 December 2006.