News | Focus February 2015 | Volume 123 | Issue 2
New Link in the Food Chain? Marine Plastic Pollution and Seafood Safety
Background image: © Steve Trewhella/FLPA/Corbis
Nate Seltenrich covers science and the environment from Petaluma, CA. His work has appeared in High Country News, Sierra, Yale Environment 360, Earth Island Journal, and other regional and national publications.
Citation: Seltenrich N. 2015. New link in the food chain? Marine plastic pollution and seafood safety. Environ Health Perspect 123:A34–A41; http://dx.doi.org/10.1289/ehp.123-A34
News Topics: Bisphenol A (BPA), Dioxins and Furans, Ecology and Wildlife, Endocrine Disruptors, Flame Retardants, Food Safety and Regulation, Marine and Coastal Science, Nanomaterials, Personal Care Products, Phthalates, Plastics, Polybrominated Diphenyl Ethers (PBDEs), Polychlorinated Biphenyls (PCBs), Polycyclic Aromatic Hydrocarbons (PAHs)
Published: 1 February 2015
An erratum has been published.
Related EHP Article
In recent years plastic pollution in the ocean has become a significant environmental concern for governments, scientists, nongovernmental organizations, and members of the public worldwide. A December 2014 study derived from six years of research by the 5 Gyres Institute estimated that 5.25 trillion plastic particles weighing some 269,000 tons are floating on the surface of the sea.1
At the same time, plastics in consumer products have become subject to increasing scrutiny regarding their potential effects on human health. Bisphenol A (BPA),2 a component of polycarbonate plastics and suspected endocrine disruptor, is one of the most widely known chemicals of interest. But BPA is only one of many monomers, plasticizers, flame retardants, antimicrobials, and other chemicals used in plastics manufacturing3 that are able to migrate into the environment.
At the junction of these two lines of inquiry is an emerging third field that is in many ways even more complex and less well understood: investigating human exposures to and potential health effects of plastics that have entered the marine food chain. Studies have demonstrated plastics’ tendency to sorb (take up) persistent, bioaccumulative, and toxic substances, which are present in trace quantities in almost all water bodies.4 The constituents of plastics, as well as the chemicals and metals they sorb, can travel into the bodies of marine organisms upon consumption,5,6,7,8,9 where they may concentrate and climb the food chain, ultimately into humans. This topic has attracted interest and funding from the U.S. Environmental Protection Agency (EPA), the National Oceanic and Atmospheric Administration (NOAA), and the National Academy of Sciences (NAS), as well as researchers, nonprofit groups, and institutions around the world.
At this point “there are more questions than answers,” says Richard Thompson, a professor of marine science and engineering at England’s Plymouth University. Thompson coined the term “microplastics” in 200410 and later undertook a three-year study of these particles in the marine environment for the UK’s Department of Environment, Food, and Rural Affairs.11,12,13 “From a human perspective,” he says, “at the moment I think there’s cause for concern rather than cause for alarm.”
Viewpoints on the human health risks of marine debris are nearly as complex as the underlying science, as was evident at an inaugural EPA and NAS symposium on the topic held in Washington, DC, in April 2014. In addition to myriad small details, the researchers in attendance considered an overarching question: Within the context of limited oceanographic research funding, the variety of other problems affecting ocean health (including overfishing and acidification), and the extent of humans’ daily and direct exposures to potentially harmful chemicals from consumer plastics and other sources—how concerned should we be about marine plastics as far as human health goes?
Researchers don’t yet have an answer, even if they believe they’re asking the right question. As EPA chemist Richard Engler concluded in a 2012 review, “While current research cannot quantify the amount, plastic in the ocean does appear to contribute to [persistent, bioaccumulative, and toxic substances] in the human diet.”14
The path from plastic pollution to chemical exposure through seafood is a long one, figuratively and often literally, and tracing all the individual steps in that theoretical journey is not the same as identifying human health effects, researchers say. Actual exposures, which are determined by innumerable variables along the way, including seafood consumption, still need to be quantified. Then these levels must be evaluated within broader contexts of consumer plastic use and environmental pollutant levels.
Exposures to plastic debris have been clearly documented for marine organisms at all trophic levels (i.e., positions within the food chain), says Bradley Clarke, a lecturer at RMIT University in Melbourne, Australia. “What remains to be determined is whether this exposure increases the body burden of … marine organisms in the natural environment and if it does, by what magnitude,” Clarke says.
There is a lack of controlled experimental work completed on the topic, Clarke adds, and it’s very difficult to disentangle pollutant exposures and bioaccumulation via plastic versus food and environmental sources. Uncertainties also surround the transfer of plastic additives to marine organisms and resultant human exposures through seafood.
We do know that plastic has become nearly ubiquitous on the planet. It has washed up on the most remote beaches, amassed in distant gyres, and been discovered in the bodies of dead organisms from fish to birds to whales.15,16
Numerous efforts have sought to quantify the amount of plastics floating on or present throughout the ocean environment, and they’ve arrived at vastly different numbers. The 5 Gyres paper1 was preceded in July 2014 by a similar study suggesting that between 7,000 and 35,000 tons of plastic are floating on the ocean’s surface.17
Anna-Marie Cook, one of two EPA lead scientists investigating the potential health effects of marine plastics, believes that estimates calculated through the use of surface trawl nets, including both of the recent global studies, vastly underestimate the scope of the problem. “Slightly more than half of all plastic is negatively buoyant, meaning that it will sink upon reaching the ocean, either into the near-shore sediment environment or to the ocean floor,” she explains. “Surface trawls do not account for the fraction of plastic in sediments, on the ocean floor, or suspended past the top few feet of the water column.”
World plastics production has experienced almost constant growth for more than half a century, rising from approximately 1.9 tons in 195018 to approximately 330 million tons in 2013.19 The World Bank estimates that 1.4 billion tons of trash are generated globally each year, 10% of it plastic.20 The International Maritime Organization has banned the dumping of plastic waste (and most other garbage) at sea.21 However, an unknown portion of the plastic produced each year escapes into the environment—instead of being landfilled, incinerated, or recycled20—and at least some of it eventually makes its way to sea.
Plastics that reach the ocean will gradually break down into ever-smaller pieces due to sunlight exposure, oxidation, and the physical action of waves, currents, and grazing by fish and birds.22 So-called microplastics—variably defined in the scientific literature and popular press as smaller than 1 or 5 mm in diameter—are understood to be the most abundant type of plastic in the ocean. The 5 Gyres authors found microplastics almost everywhere they sampled, from near-shore environments to the open ocean, in varying concentrations, and they estimated that particles 4.75 mm or smaller—about the size of a lentil—made up roughly 90% of the total plastic pieces they collected.1
But the degradation of larger pieces of plastic is not the only way microplastics end up in the ocean. Nurdles—the plastic pellets used as a feedstock for producing plastic goods—can spill from ships or land-based sources,23 and “microbeads” used as scrubbing agents in personal care products such as skin cleansers, toothpastes, and shampoos, can escape water-treatment facilities and pass into watersheds with treated water.24 (In June 2014, Illinois became the first U.S. state to ban the manufacture and sale of products containing microbeads,25 which have been documented in the Great Lakes26 and Chicago’s North Shore Channel.27)
Due to their hydrophobic nature, persistent organic chemicals—including polycyclic aromatic hydrocarbons (PAHs),28 polychlorinated biphenyls (PCBs),29 polybrominated diphenyl ethers (PBDEs),30 dioxins,31 and DDT32—have been shown to preferentially sorb to plastics when they encounter them in the ocean.33,34 Potentially thousands of such chemicals exist in the environment,35 but researchers are limited to screening for compounds they can actually identify, Bradley says.
The extent and rate of sorption can vary widely depending on the chemical, plastic type, and other variables, but plastic particles recovered from the ocean have been found to contain pollutant concentrations orders of magnitude higher than the water from which they were collected.14,36,37
Marine organisms throughout the food chain commonly consume plastics of various sizes.38,39 The tiniest microplastics are small enough to be mistaken for food by zooplankton,40 allowing them to enter the food chain at very low trophic levels. Some larger predators are thought to confuse nurdles (which typically measure less than 5 mm in diameter) with fish eggs or other food sources.41
Once plastics have been consumed, laboratory tests show that chemical additives and adsorbed pollutants and metals on their surface can desorb (leach out) and transfer into the guts and tissues of marine organisms.14 Some researchers speculate that chemicals already present in the organism may also be able to travel in the opposite direction by sorbing to plastics in the gut, depending on the concentration gradients. Yet neither process has been proven to occur in the natural environment.
We already know that many chemicals of concern are present in the seafood we eat, particularly in higher-level predators such as tuna and swordfish.42 Research has shown that harmful and persistent substances can both bioaccumulate (or increase in concentration as exposures persist) and biomagnify (or increase in concentration at higher trophic levels) within organisms as they assume some of the chemical burden of their prey or environment. Yet again, no research has yet demonstrated the bioaccumulation of sorbed pollutants in the environment.
Three key questions remain to be determined. To what extent do plastics transfer pollutants and additives to organisms upon ingestion? What contribution are plastics making to the contaminant burden in organisms above and beyond their exposures through water, sediments, and food? And, finally, what proportion of humans’ exposure to plastic ingredients and environmental pollutants occurs through seafood? Researchers are moving carefully in the direction of answers to these questions.
Human Health Questions
Among U.S. agencies, the EPA is delving into the science to answer key questions around marine plastics and human health. In addition to convening the April meeting and producing a forthcoming white paper on its findings, the agency collaborates with and directly funds researchers in the field. Staff from the EPA and the U.S. Fish and Wildlife Service are currently developing a risk assessment to quantify the chemical loading effects of plastic litter on marine life.43 And by 2016, the EPA plans to launch a similar long-term inquiry into effects on human health, including an evaluation of outcomes such as fetal formation, says Cook.
Any study of human health effects will likely depend on the cooperation of a subject community where many types of seafood are heavily consumed. “We have to have a potential threat and a potential receptor present in a location and a community who is willing to work with us on it,” Cook says. “There are a lot of repercussions to a community to find out that their food supply is potentially contaminated.” The agency also expects to award a new four-year marine debris research contract designed to gain a better understanding of the movement, distribution, and quantity of plastics off the remote northwestern Hawaiian islands.
Researcher Chelsea Rochman of the University of California, Davis, collaborated with Cook and the EPA on a 2014 study that showed an association between concentrations of certain PBDEs in fish and levels of plastic debris accumulation in the South Atlantic Ocean.44 However, no such association was seen for concentrations of BPA, alkylphenols, alkylphenol ethoxylates, or PCBs in fish.44
Rochman is also working on a separate study funded through NOAA’s Marine Debris program. The aim of the NOAA study is to demonstrate for the first time the biomagnification in marine organisms of chemicals introduced via plastics. This highly controlled laboratory experiment involves feeding contaminated plastic pellets to mussels, feeding the mussels to sturgeon, and then testing levels of PCBs within the bodies of the sturgeon. Results are still awaiting analysis and publication.
One of Rochman’s collaborators on the project, researcher Mark Browne of the University of California, Santa Barbara, recently received a grant from the Australian Research Council for a three-year program addressing another question in the field: Beyond leaching chemicals, what do plastic particles do when they enter an organism? Browne showed in 2008 that microplastics sized 3.0 and 9.6 µm in diameter can travel beyond a mussel’s gut and into its circulatory system and hemocytes (immune cells), where they may remain for a relatively long period of time—in his study, more than 48 days.45 A 2012 study by another group showed that microplastics taken up by mussels resulted in a strong inflammatory response.46
The implications of these findings for humans that consume organisms containing microplastics are not yet understood. Browne says his team is currently working to develop a method to test human tissues for microplastics. “We think that’s going to be a big turning point,” he says.
Ecotoxicologist Heather Leslie of VU University Amsterdam is among those concerned about the particle toxicity of microplastics themselves. Even without chemical hitchhikers, she says, plastic particles can induce immunotoxicological responses, alter gene expression, and cause cell death, among other adverse effects. “Exposed organisms then deal not only with chemical stress through multiple exposure routes, but also particle stress,” she explains. Leslie is currently studying the distribution and environmental fate of microplastics from cosmetics and other sources and potential toxicological effects on marine organisms in Europe’s multinational CleanSea Project.
A large body of literature about the mobility of nanoparticles offers a glimpse at how nano-size plastic particles may behave in the human body, Leslie says. “They can pass through the placenta and the blood–brain barrier and can be taken up in the gastrointestinal tract and lungs, potential sites where harm can occur,” she says. “There is a lot to learn about microplastics from the fields of particle toxicity and drug delivery technologies that apply to polymeric nanoparticles.”
In another example of ongoing research, Robert Hale, a professor at the Virginia Institute of Marine Science, has funding from both the EPA and NOAA to investigate how particle size, weathering, biofouling (the accumulation of living organisms on wet surfaces), and water characteristics including temperature, salinity, and organic carbon content influence both the sorption of organic contaminants to and the release of various additives from different types of microplastics.47 “You look at these simple parameters together, and it can get very complex,” Hale says. The EPA is particularly interested in evaluating the release of flame retardant additives from plastics, he notes, and may pursue development of a protocol to be used by manufacturers to provide data on chemical migration.
A Matter of Perspective?
Government, academic, and independent sources interviewed for this article almost unanimously expressed a mix of skepticism and concern toward the thought of ocean plastics posing a human health risk. Without exception, they also advocated for further research. A common viewpoint is that although definitive evidence does not yet exist for real-world human health impacts tied to marine plastic debris, this doesn’t prove the hypothesis null, nor does it mean there aren’t other valid reasons to address the long-lived plastic litter that washes into the world’s oceans every year.
Many researchers pointed to the need to maintain perspective on the issue. Human exposure to microplastics and plastic additives is more likely to stem from intact goods prior to disposal than from seafood, Thompson says. Clothing fibers make up a large proportion of the microplastic found worldwide, says Browne,48 and even drinking water and foods such as honey can be contaminated with microplastics, according to Leslie.
Kara Lavender Law, a research professor of oceanography with the Sea Education Association in Woods Hole, Massachusetts, who collaborated with Richard Thompson on a recent summary of current knowledge about microplastics,49 says that while overfishing and direct exposure to consumer plastics concern her more than the marine-plastic pathway, the latter still warrants investigation. “I think it’s something worth working on,” she says. “Just because we don’t see it doesn’t mean it’s not there.”
In the case of plastic constituents thought to affect the human endocrine system, any level of exposure, no matter the route, may be potentially harmful, says Carol Kwiatkowski, executive director of The Endocrine Disruption Exchange. Endocrine disruptors have shown evidence of a nonlinear or nonmonotonic dose response,50 meaning tiny doses may have larger effects than mid-level doses.
“Anything that interferes with hormone action potentially has an effect at a very low dose, because the endocrine system is designed to function at very small doses,” Kwiatkowski says. “So it’s possible this pathway could bring some exposure. You’d have to find some evidence that the chemicals were being carried through marine organisms and making it into people.”
From there, she says, researchers would still need to learn how any such exposures relate to or interact with other exposures to endocrine disruptors, including rapidly metabolized chemicals such as BPA and phthalates, and longer-lived additives such as flame retardants. In other words, to what extent do all these exposures add up, and how does that cumulative exposure translate to health outcomes? “It’s difficult to study additive effects,” Kwiatkowski says. “But it’s very important research to conduct.”
Nonetheless, the end goal, sources say, is not to abandon the use of plastic. “The benefits of plastics can be realized without the need for emission [to the ocean], ” Thompson says. “And for me that’s the tipping point for taking policy action.” New laws, for example, could require handling plastics more responsibly at the end of their useful life through recycling, proper disposal, and extended producer responsibility.
Rolf Halden, director of the Center for Environmental Security at the Biodesign Institute at Arizona State University, advocates for another solution: manufacturing more sustainable plastics from the start.51 “We need to design the next generation of plastics to make them more biodegradable so that they don’t have a long half-life, they don’t accumulate in the oceans, and they don’t have the opportunity to collect chemicals long-term,” he says. “There’s just no way we can shield people from all exposures that could occur. Let’s design safer chemicals and make the whole problem moot.”
1. Eriksen M, et al. Plastic pollution in the world’s oceans: more than 5 trillion plastic pieces weighing over 250,000 tons afloat at sea. PLoS ONE 9(12):e111913 (2014); doi: 10.1371/journal.pone.0111913.
2. EPA. Bisphenol A (BPA) Action Plan Summary [website]. Washington, DC:U.S. Environmental Protection Agency (updated 29 January 2014). Available: http://www.epa.gov/oppt/existingchemicals/pubs/actionplans/bpa.html [accessed 28 January 2015].
3. Deanin RD. Additives in plastics. Environ Health Perspect 11:35–39 (1975); http://www.ncbi.nlm.nih.gov/pmc/articles/PMC1475198/.
4. Rochman CM, et al. Long-term field measurement of sorption of organic contaminants to five types of plastic pellets: implications for plastic marine debris. Environ Sci Technol 47(3):1646–1654 (2013); doi: 10.1021/es303700s.
5. Rochman CM, et al. Ingested plastic transfers hazardous chemicals to fish and induces hepatic stress. Sci Rep 3:3263 (2013); doi: 10.1038/srep03263.
6. Browne MA, et al. Microplastic moves pollutants and additives to worms, reducing functions linked to health and biodiversity. Curr Biol 23(23):2388–2392 (2013); doi: 10.1016/j.cub.2013.10.012.
7. Chua EM, et al. Assimilation of polybrominated diphenyl ethers from microplastics by the marine amphipod, Allorchestes compressa. Environ Sci Technol 48(14):8127–8134 (2014); doi: 10.1021/es405717z.
8. Tanaka K, et al. Accumulation of plastic-derived chemicals in tissues of seabirds ingesting marine plastics. Mar Pollut Bull 69(1–2):219–222 (2013); doi: 10.1016/j.marpolbul.2012.12.010.
9. Besseling E, et al. Effects of microplastic on fitness and PCB bioaccumulation by the lugworm Arenicola marina (L.). Environ Sci Technol 47(1):593–600 (2013); 10.1021/es302763x.
10. Thompson RC, et al. Lost at sea: where is all the plastic? Science 304(5672):838 (2004); doi: 10.1126/science.1094559.
11. Bakir A, et al. Competitive sorption of persistent organic pollutants onto microplastics in the marine environment. Mar Pollut Bull 64(12):2782–2789 (2012); doi: 10.1016/j.marpolbul.2012.09.010.
12. Bakir A, et al. Transport of persistent organic pollutants by microplastics in estuarine conditions. Estuar Coast Shelf Sci 140:14–21 (2014); doi: 10.1016/j.ecss.2014.01.004.
13. Bakir A, et al. Enhanced desorption of persistent organic pollutants from microplastics under simulated physiological conditions. Environ Pollut 185:16–23 (2014); doi: 10.1016/j.envpol.2013.10.007.
14. Engler RE. The complex interaction between marine debris and toxic chemicals in the ocean. Environ Sci Technol 46(22):12302–12315 (2012); doi: 10.1021/es3027105.
15. Safina C. No refuge: tons of trash covers the remote shores of Alaska. Yale Environment 360, Opinion section (1 July 2013). Available: http://e360.yale.edu/feature/carl_safina_gyre_tons_of_trash_covers_shores_alaska/2668/ [accessed 28 January 2015].
16. de Stephanis R, et al. As main meal for sperm whales: plastics debris. Mar Pollut Bull 69(1–2):206–214 (2013); doi: 10.1016/j.marpolbul.2013.01.033.
17. Cózar A, et al. Plastic debris in the open ocean. Proc Natl Acad Sci USA 111(28):10239–10244 (2014); doi: 10.1073/pnas.1314705111.
18. PlasticsEurope. Plastics—The Facts 2013: An Analysis of European Latest Plastics Production, Demand and Waste Data. Brussels, Belgium:PlasticsEurope AISBL (2013). Available: http://www.plasticseurope.org/Document/plastics-the-facts-2013.aspx [accessed 28 January 2015].
19. PlasticsEurope. China Leads Global Plastics Production while Europe Ranks Second [press release]. Brussels, Belgium:PlasticsEurope AISBL (12 June 2014). Available: http://goo.gl/Xgx5Is [accessed 28 January 2015].
20. Hoornweg D, Bhada-Tata P. What a Waste: A Global Review of Solid Waste Management. Washington, DC:Urban Development and Local Government Unit, World Bank (March 2012). Available: http://goo.gl/GZec84 [accessed 28 January 2015].
21. IMO. Prevention of Pollution by Garbage from Ships [website]. London, United Kingdom:International Maritime Organization (2015). Available: http://www.imo.org/OurWork/Environment/PollutionPrevention/Garbage/Pages/Default.aspx [accessed 28 January 2015].
22. Zettler ER, et al. Life in the “plastisphere”: microbial communities on plastic marine debris. Environ Sci Technol 47(13):7137–7146 (2013); doi: 10.1021/es401288x.
23. Thompson RC, et al. Plastics, the environment and human health: current consensus and future trends. Philos Trans R Soc Lond B Biol Soc 364(1526):2153–2166 (2009); doi: 10.1098/rstb.2009.0053.
24. Fendall LS, Sewell MA. Contributing to marine pollution by washing your face: microplastics in facial cleaners. Mar Pollut Bull 58(8):1225–1228 (2009); doi: 10.1016/j.marpolbul.2009.04.025.
25. State of Illinois. Governor Quinn Signs Bill to Ban Microbeads, Protect Illinois Waterways [press release]. Chicago, IL:Office of the Governor, State of Illinois (8 June 2014). Available: http://www3.illinois.gov/PressReleases/ShowPressRelease.cfm?SubjectID=3&RecNum=12313 [accessed 28 January 2015].
26. Eriksen M, et al. Microplastic pollution in the surface waters of the Laurentian Great Lakes. Mar Pollut Bull 77(1–2):177–182 (2013); doi: 10.1016/j.marpolbul.2013.10.007.
27. McCormick A, et al. Microplastic is an abundant and distinct microbial habitat in an urban river. Environ Sci Technol 48(20):11863–11871 (2014); doi: 10.1021/es503610r.
28. ATSDR. Polycyclic Aromatic Hydrocarbons (PAHs) [website]. Atlanta, GA:Agency for Toxic Substances and Disease Registry, U.S. Centers for Disease Control and Prevention (updated 3 March 2011). Available: http://www.atsdr.cdc.gov/substances/toxsubstance.asp?toxid=25 [accessed 28 January 2015].
29. EPA. Health Effects of PCBs [website]. Washington, DC:U.S. Environmental Protection Agency (updated 13 June 2013). Available: http://www.epa.gov/wastes/hazard/tsd/pcbs/pubs/effects.htm [accessed 28 January 2015].
30. EPA. Polybrominated Diphenyl Ethers (PBDEs) Action Plan Summary [website]. Washington, DC:U.S. Environmental Protection Agency (updated 8 January 2015). Available: http://www.epa.gov/oppt/existingchemicals/pubs/actionplans/pbde.html [accessed 28 January 2015].
31. EPA. Environmental Assessment: Dioxin [website]. Washington, DC:U.S. Environmental Protection Agency (updated 12 August 2010). Available: http://cfpub.epa.gov/ncea/CFM/nceaQFind.cfm?keyword=Dioxin [accessed 28 January 2015].
32. EPA. DDT [website]. Washington, DC:U.S. Environmental Protection Agency (updated 18 April 2011). Available: http://www.epa.gov/pbt/pubs/ddt.htm [accessed 28 January 2015].
33. Müller JF, et al. Partitioning of polycyclic aromatic hydrocarbons in the polyethylene/ water system. Fresenius J Anal Chem 371(6):816–822 (2001); doi: 10.1007/s002160101025.
34. Pascall MA, et al. Uptake of polychlorinated biphenyls (PCBs) from an aqueous medium by polyethylene, polyvinyl chloride, and polystyrene films. J Agric Food Chem 53(1):164–169 (2005); doi: 10.1021/jf048978t.
35. EPA. Persistent Organic Pollutants: A Global Issue, A Global Response [website]. Washington, DC:U.S. Environmental Protection Agency (updated 12 June 2014). Available: http://goo.gl/Pn5p7u [accessed 28 January 2015].
36. Rochman CM, et al. Long-term sorption of metals is similar among plastic types: implications for plastic debris in aquatic environments. PLoS ONE 9(1):e85433 (2014); doi: 10.1371/journal.pone.0085433.
37. Mato Y, et al. Plastic resin pellets as a transport medium for toxic chemicals in the marine environment. Environ Sci Technol 35(2):318–324 (2001); doi: 10.1021/es0010498.
38. Davison P, Asch RG. Plastic ingestion by mesopelagic fishes in the North Pacific Subtropical Gyre. Mar Ecol Prog Ser 432:173–180 (2011); doi: 10.3354/meps09142.
39. Murray F, Cowie P. Plastic contamination in the decapod crustacean Nephrops norvegicus (Linnaeus, 1758). Mar Pollut Bull 62(6):1207–1217 (2011); doi: 10.1016/j.marpolbul.2011.03.032.
40. Cole M, et al. Microplastic ingestion by zooplankton. Environ Sci Technol 47(12):6646–6655 (2013); doi: 10.1021/es400663f.
42. Gassel M, et al. Detection of nonylphenol and persistent organic pollutants in fish from the North Pacific Central Gyre. Mar Pollut Bull 73(1):231–242 (2013); doi: 10.1016/j.marpolbul.2013.05.014.
43. EPA. EPA and U.S. Fish and Widlife Service Partner to Protect Wildlife at Hawaii’s Tern Island [press release]. San Francisco, CA:U.S. Environmental Protection Agency, Region 9 (9 September 2014). Available: http://www.epa.gov/region9/mediacenter/tern-island/ [accessed 28 January 2015].
44. Rochman CM, et al. Polybrominated diphenyl ethers (PBDEs) in fish tissue may be an indicator of plastic contamination in marine habitats. Sci Total Environ 476–477:622–633 (2014); doi: 10.1016/j.scitotenv.2014.01.058.
45. Browne MA, et al. Ingested microscopic plastic translocates to the circulatory system of the mussel, Mytilus edulis (L.). Environ Sci Technol 42(13):5026–5031 (2008); doi: 10.1021/es800249a.
46. von Moos N, et al. Uptake and effect of microplastics on cells and tissue of the blue mussel Mytilus edulis L. after an experimental exposure. Environ Sci Technol 46(20):11327–11335 (2012); doi: 10.1021/es302332w.
47. Hale RC, et al. Ghosts in the Machine: Releases of Flame Retardants from Microplastics and Recycled Materials [abstract]. Presented at: Society of Environmental Toxicology and Chemistry North America 35th Annual Meeting, Vancouver, British Columbia, Canada, 9–13 November 2014. Brussels, Belgium, and Pensacola, FL:Society of Environmental Toxicology and Chemistry (2014). Available: http://vancouver.setac.org/wp-content/uploads/2014/10/SETAC-Vancouver-Abstracts.pdf [accessed 28 January 2015].
48. Browne MA, et al. Accumulation of microplastic on shorelines worldwide: sources and sinks. Environ Sci Technol 45(21):9175–9179 (2011); doi: 10.1021/es201811s.
49. Law KL, Thompson RC. Microplastics in the seas. Science 345(6193):144–145 (2014); doi: 10.1126/science.1254065.
50. Welshons WV, et al. Large effects from small exposures. I. Mechanisms for endocrine-disrupting chemicals with estrogenic activity. Environ Health Perspect 111(8):994–1006 (2003); http://www.ncbi.nlm.nih.gov/pubmed/12826473.
51. Halden RU. Plastics and health risks. Annu Rev Public Health 31:179–194 (2010); doi: 10.1146/annurev.publhealth.012809.103714.
52. Obbard RW, et al. Global warming releases microplastic legacy frozen in Arctic Sea ice. Earth’s Future 2(6):315–320 (2014); doi: 10.1002/2014EF000240.
53. Chan K. Hong Kong plastic pellets spill: Sinopec vows to clean up beaches. Huffington Post, Green section (9 August 2012). Available: http://www.huffingtonpost.com/2012/08/10/hong-kong-plastic-pellets-spill_n_1759119.html [accessed 28 January 2015].
Since 1993 the News section of EHP has provided readers with objective, accurate information on timely environmental health topics. After years as one of the most popular features of EHP, and as our main tool for reaching a broader audience, we felt it was time the News had its own home on our website. We are now pleased to present our brand-new page devoted exclusively to EHP News! (more…)
EHP is proud to announce that “Acute Impact of Hourly Ambient Air Pollution on Preterm Birth,” published in EHP on 29 April 2016, has been selected by the Children’s Environmental Health Network (CEHN) as its November 2016 Article of the Month. CEHN Article of the Month summaries discuss the potential policy implications of current children’s environmental health research. The CEHN summary can be viewed here.
If you’re attending the American Public Health Association (APHA) 2016 Annual Meeting and Expo in Denver (October 30–November 2), stop by the NIEHS booth (#1214) in the Exhibition Hall. Children’s Health Editor Martha M. Dimes will be available to discuss EHP submissions, Children’s Health topics, and more.
Featured Children’s Health
Veronica A. Tinney, Jerad M. Denton, Lucy Sciallo-Tyler, and Jerome A. Paulson
Jerome A. Paulson and Claire L. Barnett
Kim G. Harley, Katherine Kogut, Daniel S. Madrigal, Maritza Cardenas, Irene A. Vera, Gonzalo Meza-Alfaro, Jianwen She, Qi Gavin, Rana Zahedi, Asa Bradman, Brenda Eskenazi, and Kimberly L. Parra
Rebecca Massa Nachman, Guangyun Mao, Xingyou Zhang, Xiumei Hong, Zhu Chen, Claire Sampankanpanich Soria, Huan He, Guoying Wang, Deanna Caruso, Colleen Pearson, Shyam Biswal, Barry Zuckerman, Marsha Wills-Karp, and Xiaobin Wang