Life history and social structure as drivers of persistent organic pollutant levels and stable isotopes in Hawaiian false killer whales ( Pseudorca crassidens )

被引:13
作者
Kratofil, Michaela A. [1 ]
Ylitalo, Gina M. [2 ]
Mahaffy, Sabre D. [1 ]
West, Kristi L. [3 ,4 ]
Baird, Robin W. [1 ,3 ]
机构
[1] Cascadia Res Collect, 218 1-2 W 4th Ave, Olympia, WA 98501 USA
[2] NOAA, Environm & Fisheries Sci Div, Northwest Fisheries Sci Ctr, Natl Marine Fisheries Serv, 2725 Montlake Blvd East, Seattle, WA 98112 USA
[3] Hawaii Inst Marine Biol, POB 1346, Kaneohe, HI 96744 USA
[4] Coll Trop Agr & Human Resources, Human Nutr Food & Anim Sci, 1955 East West Rd,Ag Sci 216, Honolulu, HI 96822 USA
关键词
POPs; Cetaceans; Pacific; Carbon; Nitrogen; Endangered species; DOLPHINS TURSIOPS-TRUNCATUS; POLYBROMINATED DIPHENYL ETHERS; BROMINATED FLAME RETARDANTS; ORCINUS-ORCA; POLYCHLORINATED-BIPHENYLS; POPULATION-STRUCTURE; BODY CONDITION; BLUBBER; CETACEANS; HARBOR;
D O I
10.1016/j.scitotenv.2020.138880
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
False killer whales are long-lived, slow to mature, apex predators, and therefore susceptible to bioaccumulation of persistent organic pollutants (POPs). Hawaiian waters are home to three distinct populations: pelagic; Northwestern Hawaiian Islands (NWHI) insular; and main Hawaiian Islands (MHI) insular. Following a precipitous decline over recent decades, the MHI population was listed as endangered under the Endangered Species Act in 2012. This study assesses the risk of POP exposure to these populations by examining pollutant concentrations and ratios from blubber samples (n = 56) related to life history characteristics and MHI social clusters. Samples were analyzed for PCBs, DDTs, PBDEs, and some organochlorine pesticides. Skin samples (n = 52) were analyzed for stable isotopes delta C-13 and delta N-15 to gain insight into MHI false killer whale foraging ecology. Pollutant levels were similar among populations, although MHI whales had a significantly higher mean ratio of DDTs/PCBs than NWHI whales. The Sigma PCB concentrations of 28 MHI individuals (68%) sampled were equal to or greater than suggested thresholds for deleterious health effects in marine mammals. The highest POP values among our samples were found in four stranded MHI animals. Eight of 24 MHI adult females have not been documented to have given birth; whether they have yet to reproduce, are reproductive senescent, or are experiencing reproductive dysfunction related to high POP exposure is unknown. Juvenile/sub-adults had significantly higher concentrations of certain contaminants than those measured in adults, and may be at greater risk of negative health effects during development. Multivariate analyses, POP ratios, and stable isotope ratios indicate varying risk of POP exposure, foraging locations and potentially prey items among MHI social clusters. Our findings provide invaluable insight into the ongoing risk POPs pose to the MHI population's viability, as well as consideration of risk for the NWHI and pelagic stocks.
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页数:14
相关论文
共 101 条
[1]   A novel non-invasive tool for disease surveillance of free-ranging whales and its relevance to conservation programs [J].
Acevedo-Whitehouse, K. ;
Rocha-Gosselin, A. ;
Gendron, D. .
ANIMAL CONSERVATION, 2010, 13 (02) :217-225
[2]  
AGUILAR A, 1994, ARCH ENVIRON CON TOX, V27, P546
[3]  
[Anonymous], 1991, MARINE MAMMAL STRAND
[4]  
[Anonymous], 2017, Document PSRG-2017-16
[5]  
[Anonymous], 2018, R LANG ENV STAT COMP
[6]   Extensive Core Microbiome in Drone-Captured Whale Blow Supports a Framework for Health Monitoring [J].
Apprill, Amy ;
Miller, Carolyn A. ;
Moore, Michael J. ;
Durban, John W. ;
Fearnbach, Holly ;
Barrett-Lennard, Lance G. .
MSYSTEMS, 2017, 2 (05)
[7]   Persistent organic pollutant concentrations in blubber of 16 species of cetaceans stranded in the Pacific Islands from 1997 through 2011 [J].
Bachman, Melannie J. ;
Keller, Jennifer M. ;
West, Kristi L. ;
Jensen, Brenda A. .
SCIENCE OF THE TOTAL ENVIRONMENT, 2014, 488 :115-123
[8]  
Baird R.W., 2018, The IUCN Red List of Threatened Species, V2018, DOI [10.2305/IUCN.UK.2018-2.RLTS.T18596A50371251.en, DOI 10.2305/IUCN.UK.2018-2.RLTS.T18596A50371251.EN]
[9]  
Baird R. W., 2009, CASCADIA RES COLLECT
[10]  
Baird R.W., 2019, 67703 HAW BOARD LAND