Status and ecology of the brown pelican in the Greater Puerto Rican Bank region

dc.contributor.author Collazo, Jaime
dc.contributor.department Animal Ecology (Historical Department)
dc.date 2018-08-15T14:36:36.000
dc.date.accessioned 2020-07-02T06:08:31Z
dc.date.available 2020-07-02T06:08:31Z
dc.date.copyright Tue Jan 01 00:00:00 UTC 1985
dc.date.issued 1985
dc.description.abstract <p>The endangered Caribbean brown pelican (Pelecanus occidentalis occidentalis) was studied in the Greater Puerto Rican Bank from September 1980 to July 1983. Pelican numbers in Puerto Rican coastal waters averaged 1996 annually. Winter populations in Puerto Rico were 25% to 30% larger than summer populations because of an influx of newly fledged young and post-breeding adults from the U.S. Virgin Islands. Estimated mean annual pelican population size in the Bank region is 2300. Yearlings, subadults, and non-breeding adults tended to remain in Puerto Rican waters until breeding readiness caused their return to breeding colonies. Roosting and nesting habitat was comprised mostly of mangrove in Puerto Rico and offshore cays in the U.S. Virgin Islands. Used sites of mangrove vegetation had a mean height of 6.5 m, diameter at breast height of 13.2 cm, and stem density of 3557/ha. Feeding occurred in shallow, nutrient-rich waters associated with mangroves, estuaries, closed impoundments, and offshore cays. No relationship between pelican numbers and food availability (catchability) at selected feeding localities was detected. Pelican diet was dominated by Jenkinsia lamprotaenis, Anchoa lyolepis, and Harengula spp. Tilapia mossambica was an important prey species at estuaries and closed impoundments. Feeding success was correlated with age and water turbidity. Breeding efforts peaked during fall with extended breeding seasons in all colonies except those in western and southwestern Puerto Rico. Mean young produced per nesting attempt was 1.7 (1980), 0.59 (1981), and 0.71 (1982). These rates are believed adequate to maintain a viable population but further monitoring is recommended. Environmental contaminants, disease, climate and habitat availability are not limiting factors to pelican populations. Food and its distribution in space and time probably is the chief proximate factor influencing and regulating numbers of Caribbean pelicans.</p>
dc.format.mimetype application/pdf
dc.identifier archive/lib.dr.iastate.edu/rtd/8684/
dc.identifier.articleid 9683
dc.identifier.contextkey 6343434
dc.identifier.doi https://doi.org/10.31274/rtd-180813-8681
dc.identifier.s3bucket isulib-bepress-aws-west
dc.identifier.submissionpath rtd/8684
dc.identifier.uri https://dr.lib.iastate.edu/handle/20.500.12876/81699
dc.language.iso en
dc.source.bitstream archive/lib.dr.iastate.edu/rtd/8684/r_8604454.pdf|||Sat Jan 15 02:15:03 UTC 2022
dc.subject.disciplines Ecology and Evolutionary Biology
dc.subject.disciplines Environmental Sciences
dc.subject.keywords Animal ecology
dc.title Status and ecology of the brown pelican in the Greater Puerto Rican Bank region
dc.type dissertation
dc.type.genre dissertation
dspace.entity.type Publication
relation.isOrgUnitOfPublication dc916ec7-70d9-48fc-a9b4-83f345e17b12
thesis.degree.level dissertation
thesis.degree.name Doctor of Philosophy
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