Incorporation of anthropogenic debris into double-crested cormorant nests, Toronto, Ontario
Introduction
Anthropogenic debris pollution is ubiquitous in the natural environment (Lippiatt et al., 2013, Rochman et al., 2016), and much of the debris in marine and freshwater environments is plastic (Barnes et al., 2009). The detrimental effects of plastic pollution to wildlife is widely documented (Gall and Thompson, 2015, Gregory, 2009), yet the majority of studies are on marine birds (Provencher et al., 2015). Corcoran et al. (2015) noted the only data available on the type and quantity of plastic pollution in the Great Lakes (Lake Ontario) were produced by volunteer-led initiatives such as the Great Canadian Shoreline Cleanup and the Adopt-a-Beach Program (a U.S.-based program from the Alliance for the Great Lakes). But, evidence is mounting that suggests that freshwater birds may also be exposed to plastic pollution, particularly near major cities and industrial sites (Zbyszewski et al., 2014). For example, Holland et al. (2016) reported ingestion rates in freshwater waterfowl were similar to historical trends in marine birds and called for a monitoring program (see also Provencher et al., 2015).
Indicator species can be used to determine the impacts of anthropogenic debris pollution in aquatic environments because they are assumed to reflect exposure or response to a stressor thus providing useful information of the health condition of the ecosystem they inhabit (Canterbury et al., 2000, Kushlan, 1993, Siddig et al., 2016, Durant et al., 2009). Colonial waterbirds are considered effective indicator species because of ease of data gathering, they gather in a few locations in large numbers, and can be used to detect trends on coexisting species across food webs (Piatt et al., 2007; see also Hebert et al., 2011).
In the Great Lakes, colonial-nesting waterbirds have been used for decades to track contaminants (Bishop et al., 2016, Yamashita et al., 1993). Double-crested cormorants (Phalacrocorax auritus, hereinafter cormorants) are widely distributed across North America nesting adjacent to both freshwater and marine environments (Dorr et al., 2014). Cormorants forage in both benthic and pelagic zones (King et al., 2017), and their diet consists almost entirely of fish which makes them prone to exposure to bio-accumulative substances (e.g., Bishop et al., 2016) and to microplastics (Brookson et al., 2019). Because colonies exist throughout the Great Lakes (see Chip Weseloh et al., 2002), Provencher et al. (2015) recommended using cormorant nests as part of an inland plastics monitoring program.
One of the most common interactions between birds and anthropogenic macro debris (>2.5 cm; Lippiatt et al., 2013) is the use of these items in nest building. Incorporation of synthetic materials in birds’ nests can cause entanglement and ingestion of debris (Lavers et al., 2013, Votier et al., 2011) and negatively impact nesting and fledging success (Wang et al., 2009). In a review on wildlife entanglement, Ryan (2018) suggested that incidence of plastic in nests correlated with its local availability. Yet birds may choose anthropogenic over natural debris even when natural nesting material is available because items may: resemble natural nest material or prey color (Lavers et al., 2013, Tavares et al., 2016); be used to enhance mate attraction (Verlis et al., 2014); or be based on sexually selected colour preferences. In marine environments, debris incidence in nests appears to be primarily related to fishing efforts (Bond et al., 2012, O'Hanlon et al., 2019). While the study of anthropogenic debris in bird nests is relatively new (Battisti et al., 2019), documentation exists primarily for marine birds (black-legged kittiwakes Rissa tridactyla, Hartwig et al., 2007; Australasian gannets Morus serrator, Norman et al., 1995; northern gannets Morus bassanus, Montevecchi, 1991, Votier et al., 2011, Bond et al., 2012; kelp gulls Larus dominicanus, Witteveen et al., 2017; brown bobbies Sula leucogaster, Verlis et al., 2014, Tavares et al., 2016; and double-crested cormorants, Gulf of Maine; Podolsky and Kress, 1989) and research is lacking for freshwater systems (Holland et al., 2016, Jagiello et al., 2018).
In this study, we quantified the frequency and type of debris in cormorant nests at a colony in Lake Ontario. We compared debris proportion and type in cormorant nests to debris recorded in the Great Canadian Shoreline Cleanup (GCSC; shorelinecleanup.ca). GCSC is a citizen science program used to monitor the abundance and distribution of anthropogenic debris (see Driedger et al., 2015) and existing surveys at the study site permitted a comparison. Finally, following Provencher et al.’s (2015) recommendation, we consider if cormorant nests should be used as an indicator to monitor anthropogenic debris pollution.
Section snippets
Study area
Cormorant nest sampling and the GCSC data were from Tommy Thompson Park, Lake Ontario adjacent to Toronto, Canada’s largest city. Tommy Thompson Park is on the Leslie Street Spit, the latter of which was used as a site for depositing waste (e.g., unreinforced concrete, broken concrete, brick, ceramic tiles and clean porcelain) from city infrastructure from 1959 to 2017 (Foster, 2007). An archaeological study documented a large number of personal items and household debris (mainly electrical
Results
Seven items ≤2.5 cm, all soft plastic, were removed from the dataset as they were likely due to breakage while processing the samples. All of the nests sampled contained anthropogenic debris (100%, n = 50) with a total number of 1,435 items (average ± SD = 28.7 ± 22.0 items/nest; range 5–97) and total weight of 13,820.17 g (average ± SD = 276.4 ± 301.86 g/nest; Fig. 1). Out of 787 individual items measured, length varied from 442 cm (coiled wire) to 2.6 cm (average ± SD = 29.9 ± 30.49 cm); mass
Discussion
In this study, we found that all nests sampled contained some form of anthropogenic debris, and plastic was the most common item. Podolsky and Kress (1989) assessed 497 double-crested cormorant nests in the Gulf of Maine and found that 37% of them contained plastic, lower than what was observed in our study. However, since this study was undertaken, the incidence of plastic in marine environments has increased exponentially (Provencher et al., 2017, see also O'Hanlon et al., 2019). While
Declaration of Competing Interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgments
We thank Toronto and Region Conservation Authority for their support of cormorant research at Tommy Thompson Park, Cole Swanson for discussions on the topic of cormorants and plastic, the Great Canadian Shoreline Cleanup for the use of their data in this study, Andrew Gavloski, and Miranda Baksh for their assistance in processing the samples, Sheila Colla for the use of her lab, Hugh McCague for statistical advice, and Laurence Packer, Shane de Solla and two anonymous reviewers for comments on
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