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Marine Litter
Vital Graphics
IMPACTS
synthetic fibres), polyvinylchloride (PVC used in pipes,
bottles and non-food packaging), epoxy resins (adhesives
and metal coatings) and styrenic polymers (styrene foam
insulation) as posing the highest human health risk
(Lithner et al., 2011). These plastic polymers (apart from
epoxy resin) are amongst the most common microplastic
litter encountered in the marine environment.
Plastic, a magnet for other contaminants
and harmful organisms
In the marine environment plastic can be both a source
and sink for contaminants. As well as releasing chemicals,
microplastics have been shown to adsorb compounds
like polycyclic aromatic hydrocarbons (PAHs) and metals
from the surrounding sea water. Due to their high surface
area to volume ratio, microplastics can concentrate
contaminants to orders of magnitude higher than in the
surrounding sea water (Mato et al., 2001). Substances
referred to as persistent, bioaccumulative and toxic
(PBTs), such as dichlorodiphenyltrichloroethane (DDT),
polychlorinated biphenyls (PCBs) and persistent organic
pollutants (POPs) are of particular concern. There is
evidence that hydrophobic contaminants such as POPs
are more likely to be adsorbed onto plastic polymers than
marine sediments (Tueten et al., 2007). Furthermore, older
plastic particles have been found to have higher levels
of POPs, suggesting that they continue to adsorb and
concentrate contaminants for as long as they remain in
the marine environment (Frias et al., 2010).
The ingestion of marine debris carrying these concentrated
toxins has potential to bioaccumulate up the food chain and
enter the human diet. However, although there is evidence
of the harmful impacts of these chemicals on marine
biota and human health (in men, women and children),
there is uncertainty regarding their bioavailability once
ingested. There is little research yet available on gender-
differentiated effects of these secondary chemicals that are
transferred up the food chain to humans along with the
microbeads. Bouwmeester et al. (2015) conclude that, from
available evidence, the dietary intake of POPs and other
additives adhering to marine microplastics will constitute
a minor component of exposure to these contaminants
compared to other exposure pathways (such as ingestion
of crops treated with herbicide, burning of waste, chemical
fires and industrial exposure).
Mussel culture Oyster culture Because they lter water, bivalves (such as mussels, oysters, clams and others) can absorb and excrete microplastic present in the sea water where they are cultivated After harvesting, shell sh are usually kept in clean water to get rid of contaminants. The shell sh expel some microplastics, while others remain inside, reach the market and end up on the consumer’s plate Nutrients Microplastics Sea water inhaled Water exhaled Sea water inhaled Water exhaled An example of howmicroplastics could end up on a consumer's plate Sources:Tjärnö Marine Biological Laboratory, Strömstad, Sweden; personal communication with Dr. Sarah Dudas Mussel culture Oyster culture Because they lter water, bivalves (such as mussels, oysters, clams and others) can absorb and excrete microplastic present in the sea water where they are cultivated After harvesting, shell sh are usually kept in clean water to get rid of contaminants. The shell sh expel some microplastics, while others remain inside, reach the market and end up on the consumer’s plate Nutrients Microplastics Sea water inhaled Water exhaled Sea water inhaled Water exhaled An example of howmicroplastics could end up on a consumer's plate Sources:Tjärnö Marine Biological Laboratory, Strömstad, Sweden; personal communication with Dr. Sarah Dudas