Pl. Flint et al., Modeling bird mortality associated with the M/V Citrus oil spill off St. Paul Island, Alaska, ECOL MODEL, 117(2-3), 1999, pp. 261-267
We developed a model to estimate the number of bird carcasses that were lik
ely deposited on the beaches of St. Paul Island, Alaska following the M/V C
itrus oil spill in February 1996. Most of the islands beaches were searched
on an irregular schedule, resulting in the recovery of 876 King Elder carc
asses. A sub-sample of beaches were intensively studied to estimate daily p
ersistence rate and detection probability [Fowler, A.C., Flint, P.L., 1997.
Marine Pollution Bulletin]. Using these data, our model predicted that an
additional 733 +/- 70 King Elder carcasses were not detected during our sea
rches. Therefore, we estimate that at least 1609 +/- 70 King Elder carcasse
s occurred on beaches as a result of the spill. We lacked sufficient sample
size to model losses for other species, thus we applied the estimated reco
very rate for King Elders (54%) to other species and estimate a total combi
ned loss of 1765 birds. In addition, 165 birds were captured alive making t
he total estimated number of birds impacted by the M/V Citrus spill 1930. G
iven that oiled birds occurred in places on the island which could not be s
ystematically searched combined with the fact that it was unlikely that oil
ed birds that died at sea would have been recovered during our searches [Fl
int, P.L., Fowler, A.C., 1998. Marine Pollution Bulletin], our estimate of
total mortality associated with the spill should be considered a minimum. (
C) 1999 Elsevier Science B.V. All rights reserved.