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Research Article

Threat of plastic pollution to seabirds is global, pervasive, and increasing

Chris Wilcox, Erik Van Sebille, and Britta Denise Hardesty
  1. aOceans and Atmosphere Business Unit, Commonwealth Scientific and Industrial Research Organisation, Hobart, TAS 7001, Australia;
  2. bGrantham Institute & Department of Physics, Imperial College London, London SW7 2AZ, United Kingdom;
  3. cAustralian Research Council Centre of Excellence for Climate System Science, University of New South Wales, Sydney, NSW 2052, Australia

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PNAS September 22, 2015 112 (38) 11899-11904; first published August 31, 2015; https://doi.org/10.1073/pnas.1502108112
Chris Wilcox
aOceans and Atmosphere Business Unit, Commonwealth Scientific and Industrial Research Organisation, Hobart, TAS 7001, Australia;
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  • For correspondence: chris.wilcox@csiro
Erik Van Sebille
bGrantham Institute & Department of Physics, Imperial College London, London SW7 2AZ, United Kingdom;
cAustralian Research Council Centre of Excellence for Climate System Science, University of New South Wales, Sydney, NSW 2052, Australia
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Britta Denise Hardesty
aOceans and Atmosphere Business Unit, Commonwealth Scientific and Industrial Research Organisation, Hobart, TAS 7001, Australia;
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  1. Edited by James A. Estes, University of California, Santa Cruz, CA, and approved July 2, 2015 (received for review January 31, 2015)

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    Fig. 1.

    Plastic ingestion by seabirds as reported in the literature (1962–2012). (A) Frequency of individuals with plastic fragments in their digestive system per species–study combination. (B) Proportion of individuals in each species–study combination having plastic in their digestive system with time. Plot shows median and quartiles, with bars extending to 1.5 times the interquartile range. (C) Date of first discovery of plastic ingestion for seabird species across all species identified in the literature review.

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    Fig. 2.

    The expected number of seabird species ingesting plastic and driving factors. Predictions are at the 1 × 1 degree scale. (A) The expected number of species ingesting plastic based on predictions from a generalized linear mixed model, using a random effect to represent taxa-specific ingestion rates (n = 186). (B) The expected number of species ingesting plastic, as in A, but based on a generalized linear model using fixed effects for taxa-specific ingestion rates (n = 92). (C) Modeled concentration of marine debris in the world’s oceans on a log scale. (D) Species richness for seabirds considered in this study, based on data from Birdlife International (32).

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    Table 1.

    Changes in plastic ingestion reported in the literature for seabirds

    A. Incidence of plastic in individual seabirds within a study
    Fixed EffectsRandom Effects
    TermCoefficient EstimateStandard ErrorZ valuePr(>|z|)Number of groupsModel TermGrouping VariableVariance
    Intercept−3.080.61−5.034.87E-0759InterceptReference4.30
    Year*1.760.384.584.63E-0657InterceptGenus8.61
    Method Lavage0.240.310.760.4557Year*Genus0.92
    Method Bolus−0.290.37−0.790.43
    Method Necropsy−0.290.25−1.190.24
    B. Chance of identifying a species that has ingested plastic
    Fixed EffectsRandom Effects
    TermCoefficient EstimateStandard ErrorZ valuePr(>|z|)Number of groupsModel TermGrouping VariableVariance
    Intercept1.320.572.300.02159InterceptReference0.48
    Year*0.800.292.730.006357InterceptGenus2.55
    Method Lavage−1.710.86−1.990.04657Year*Genus0.019
    Method Bolus−0.931.20−0.780.44
    Method Necropsy−1.360.55−2.480.013
    • ↵* Year is centered and rescaled for analysis, (year – 1982.365)/10.43.

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    Table 2.

    Analysis of the predictive power of debris exposure for predicting ingestion rates reported in the scientific literature

    A. Comparison of model adequacyB. Parameters for the best model
    ModelAICCoefficientCoefficientStd. ErrorPr(>|z|)
    DSGT2656.8Intercept−96.886.41< 2e−16
    SGT2679.0Weighted Mean0.00320.00071.1e−06
    DGT2688.3Body Size2.720.477.5e−09
    DSG2871.9G Aphrodroma−1.640.742.6e−02
    SG2900.1G Calonectris−1.780.304.3e−09
    GT2904.1G Cyclorrhynchus3.330.20< 2e−16
    DG2910.9G Fratercula0.560.218.9e−03
    G3180.2G Fulmarus1.260.233.9e−08
    DT4778.5G Oceanodroma1.430.368.6e−05
    DST4780.5G Pachyptila1.080.351.9e−03
    ST5473.2G Pelagodroma2.770.517.0e−08
    T5513.0G Phoebastria−5.461.271.6e−05
    DS6010.9G Procellaria−2.060.471.4e−05
    D6117.3G Pseudobulweria−3.241.021.5e−03
    S6158.6G Pterodroma−1.350.241.2e−08
    07982.2G Spheniscus−11.782.059.7e−09
    G Thalassarche−7.241.043.4e−12
    Year0.0470.003< 2e−16
    Method L−7.111.023.0e−12
    Method LN−2.640.29< 2e−16
    Method N0.440.091.1e−06
    • Note that genera and sampling methods that did not have significant coefficients are not reported for brevity. Note that the reference genus is Aethia, which is represented in the data by 3 species sampled in Alaska, and is included in the intercept term in the model. Coefficients for genera included in the analysis are preceded by a “G” and italicized. D, debris exposure; G, genus; S, body weight; T, starting year of the study; 0, intercept only model. Sampling method codes are: L, lavage; N, necropsy.

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Plastic in seabirds is pervasive and increasing
Chris Wilcox, Erik Van Sebille, Britta Denise Hardesty
Proceedings of the National Academy of Sciences Sep 2015, 112 (38) 11899-11904; DOI: 10.1073/pnas.1502108112

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Plastic in seabirds is pervasive and increasing
Chris Wilcox, Erik Van Sebille, Britta Denise Hardesty
Proceedings of the National Academy of Sciences Sep 2015, 112 (38) 11899-11904; DOI: 10.1073/pnas.1502108112
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