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28 MINEAU Eq7 AI.. VOL. 33, NO. 1<br />

Table 14. Continued.<br />

SPECIES LOCATION PERIOD<br />

NO.<br />

BIRDS<br />

RECEIVED<br />

NATURE OF DIAGNOSTICS<br />

Bald Eagle'<br />

Great Horned Owl i<br />

Virginia<br />

Virginia<br />

1985-90<br />

1985-90<br />

14<br />

21<br />

Blood ChE. Exposure inferred<br />

from discontinuous (bimodal)<br />

distribution <strong>of</strong> activity levels <strong>and</strong><br />

strong correlation between reduced<br />

levels <strong>and</strong> symptoms <strong>of</strong> intoxication,<br />

ataxia being the most<br />

common. No chemical confirma-<br />

tion.<br />

Blood ChE. Exposure inferred<br />

from discontinuous (bimodal)<br />

distribution <strong>of</strong> activity levels <strong>and</strong><br />

strong correlation between reduced<br />

levels <strong>and</strong> symptoms <strong>of</strong> intoxication,<br />

ataxia being the most<br />

common. No chemical confirma-<br />

tion.<br />

Turkey Vulture'<br />

Virginia<br />

1985-90<br />

21<br />

Blood ChE. Exposure inferred<br />

from discontinuous (bimodal)<br />

distribution <strong>of</strong> activity levels <strong>and</strong><br />

strong correlation between reduced<br />

levels <strong>and</strong> symptoms <strong>of</strong> intoxication,<br />

ataxia being the most<br />

common. No chemical confirma-<br />

tion.<br />

Franson et al. (1996).<br />

Franson et al. (1995).<br />

Gremillion-Smith <strong>and</strong> Wo6lf (1993).<br />

Franson <strong>and</strong> Little (1996).<br />

Work <strong>and</strong> Hale (1996).<br />

F•x <strong>and</strong> Barrows (1990).<br />

Hosea pers. comm.<br />

L.K. Wilson pers. comm.<br />

S L. Porter pers. comm.<br />

Monitoring. The value <strong>of</strong> collecting <strong>and</strong> making<br />

data available on incidents is critical for the cred-<br />

•bfiity <strong>of</strong> any pesticide-regulatory system. Unfortunately,<br />

very few jurisdictions are currently assembling<br />

this information, let alone providing the<br />

resources needed for adequate investigation. Also<br />

critical is the regulatory system's ability or willingness<br />

to respond to problems that are identified. A<br />

recent success has been the Argentine government's<br />

willingness to take rapid action on monocrotophos.<br />

This is in contrast to the slow pace <strong>of</strong><br />

regulatory action on problem chemicals such as<br />

carb<strong>of</strong>uran, famphur <strong>and</strong> fenthion in North Amer-<br />

ica. Also, the recent monocrotophos incidents reinforced<br />

the interconnectedness <strong>of</strong> countries <strong>and</strong><br />

indicated that we should not become complacent<br />

about products that have been canceled or otherwise<br />

regulated or which may never have been registered<br />

in North America or Europe. Many <strong>of</strong> these<br />

products continue to be used heavily in developing<br />

countries.<br />

The biggest problem we encountered in preparing<br />

this assessment was the lack <strong>of</strong> detail supplied<br />

<strong>with</strong> many incidents. It is critical that all available<br />

data be made available to researchers <strong>and</strong> analysts<br />

to allow meaningful conclusions to be drawn con-

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