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Marine pollution: the future challenge is to link human and wildlife studies. (Guest Editorial).


The rapid population growth and enormous urban and coastal development in many of the world's coastal regions have caused considerable concern that anthropogenic an·thro·po·gen·ic  
adj.
1. Of or relating to anthropogenesis.

2. Caused by humans: anthropogenic degradation of the environment.
 pollution may reduce biodiversity and productivity of marine ecosystems, resulting in reduction and depletion of human marine food resources. In addition, natural environments are important for recreation, and consequently for human health and welfare, and there is now increased awareness that nature has its own intrinsic value. Pollution reduces the aesthetic value and perhaps also the intrinsic value of the marine environment, whether the pollution is visual (such as oil pollution and plastic debris) or invisible (such as chemical compounds).

Another main reason for concern about marine pollution is related to the direct effects of pollution on human health. Because many pollutants accumulate in marine organisms, humans are exposed to pollutants when they consume food from polluted areas. Several studies have documented that human populations that consume large amounts of marine food have high burdens of persistent organic pollutants (POPs), such as dioxins, furans, polychlorinated biphenyls (PCBs), and some heavy metals. There has been a particular focus on indigenous people who consume large amounts of marine food, including blubber products of marine mammals (Dewailly et al. 1999).

Because construction of treatment facilities for sewage is unlikely to catch up with increasing human activities, especially in developing countries, eutrophication eutrophication (ytrō'fĭkā`shən), aging of a lake by biological enrichment of its water. In a young lake the water is cold and clear, supporting little life.  and hypoxia hypoxia

Condition in which tissues are starved of oxygen. The extreme is anoxia (absence of oxygen). There are four types: hypoxemic, from low blood oxygen content (e.g., in altitude sickness); anemic, from low blood oxygen-carrying capacity (e.g.
 will be a persistent problem. Also, exposure of marine organisms to increasing concentrations of human bacteria may pose a threat to coastal ecosystems. High levels of natural and synthetic compounds with estrogenic properties in sewage effluents have been linked to feminization feminization /fem·i·ni·za·tion/ (fem?i-ni-za´shun)
1. the normal development of primary and secondary sex characters in females.

2. the induction or development of female secondary sex characters in the male.
 of fish. There is also concern about other chemicals with endocrine-disrupting properties. One example is the marine antifouling paint ingredient tributyltin, which has been shown to cause imposex in gastropods, to affect coastal and estuarine es·tu·a·rine  
adj.
1. Of, relating to, or found in an estuary.

2. Geology Formed or deposited in an estuary.

Adj. 1. estuarine - of or relating to or found in estuaries
estuarial
 molluscs populations, and to cause reduction of species diversity in marine estuarine benthic ben·thos  
n.
1. The collection of organisms living on or in sea or lake bottoms.

2. The bottom of a sea or lake.



[Greek.
 and epibenthic invertebrate invertebrate (ĭn'vûr`təbrət, –brāt'), any animal lacking a backbone. The invertebrates include the tunicates and lancelets of phylum Chordata, as well as all animal phyla other than Chordata.  communities (Matthiessen and Law 2002). Until now, most studies concerned with the effects of marine pollution have focused on biochemical and physiologic effects. In the future, studies should address the effects of pollution on behavioral traits that can potentially alter biodiversity and ecosystem functioning. Examples of such ecologically significant behavioral traits are antipredator behavior, reproductive behavior, parental behavior, and feeding success (Wibe 2003).

Recent reports have documented dose relationships between mercury, dioxins, furans, and PCBs and several reproductive, cognitive, and neurologic factors in humans. Obviously, there is a clear need to pursue such studies, and there is a particular need to identify possible confounding factors. Breast-feeding breast-feeding /breast-feed·ing/ (brest´fed?ing) nursing; the feeding of an infant at the mother's breast.  and the quality of the home environment are examples of identified confounding factors that may modify and actually counteract harmful effects of POPs (Jacobson and Jacobson 2002; Walkowiak et al. 2001).

Many marine mammals are highly dependent on well-developed cognitive abilities and must have a normal behavior to survive. The selection against cognitive and neurologic dysfunction or retardation is most likely much more significant in wildlife than in humans. Thus, there is also a great need for wildlife studies that focus on the effects of marine pollution on cognitive abilities and related neurologic effects, and it is of great interest how such effects can affect biodiversity and ecosystem functioning.

The harmful effects of many POPs on human and environmental health have been recognized, and in 2000, an international ban was implemented on the 12 most noxious POPs, the so-called "dirty dozen" (Kaiser and Enserink 2000). During the last two decades, the concentrations of many pollutants in marine biota biota /bi·o·ta/ (bi-o´tah) all the living organisms of a particular area; the combined flora and fauna of a region.

bi·o·ta
n.
The flora and fauna of a region.
 have declined. However, every year thousands of new synthetic chemicals are produced, and recently there have been reports of so called "novel" POPs in humans and in marine biota. The best known are brominated flame retardants (BFRs), such as polybrominated diphenyl ethers Polybrominated diphenyl ethers or PBDE, are a flame retardant sub-family of the brominated flame retardant group. They have been used in a wide array of household products, including fabrics, furniture, and electronics.  (De Wit 2002). The capacity of these chemicals to bioaccumulate, biomagnify, and provoke effects in marine organisms and humans is still unclear. This is also the case for other "novel" POPs such as perfluorooctane sulfonate sul·fo·nate
n.
A salt or ester of sulfonic acid.

v.
1. To introduce one or more sulfonic acid groups into an organic compound.

2. To treat with sulfonic acid.
 and polychloronaphtalenes, which have been detected in marine food webs (Corsolini et al. 2002; Giesy and Kannan 2001). These pose a new threat to the health of individuals and both human and wildlife populations.

Arctic animals live far from most pollution sources, but some species such as the polar bear (Ursus maritimus) and the beluga beluga (bəl`gə) or white whale, small, toothed northern whale, Delphinapterus leucas. The beluga may reach a length of 19 ft (5.  whale (Delphinapterus leucas) have been reported to have very high levels of some POPs (Andersen et al. 2001; Norstrom et al. 1998). This is due to a combination of their trophic trophic /tro·phic/ (tro´fik) (trof´ik) pertaining to nutrition.

troph·ic
adj.
Of, relating to, or characterized by nutrition.
 position in the Arctic marine food web and the fact that POPs are transported to the Arctic via the atmosphere. In beluga whales, exposure to polycyclic aromatic hydrocarbons has been linked to high rates of cancer (Martineau et al. 2002). In the polar bear there are indications that thyroid and sex hormones, retinols, and immune function are affected by POPs (Haave et al. 2003; Skaare et al. 2002). However, it is still unclear if populations of these species are at risk due to marine pollution.

In studies concerning health effects of marine pollution on humans and on wildlife, there is often a range of confounding intrinsic and extrinsic factors (De Guise et al. 2001) that can make it difficult to provide clear evidence that populations or subpopulations are affected by marine pollution. To obtain better knowledge of effects of marine pollution on populations, more focus should be put on integrating results from human and wildlife studies, which are often viewed separately. This will help to identify important confounding factors and to improve background knowledge for hazard assessment with respect to effects of marine pollution on the health of individuals and human and wildlife populations.

REFERENCES

Andersen G, Kovacs KM, Lydersen C, Skaare JU, Gjertz I, Jenssen BM. 2001. Concentrations and patterns of organochlorine or·gan·o·chlo·rine
n.
Any of various hydrocarbon pesticides, such as DDT, that contain chlorine.
 contaminants in white whales (Delphinapterus leucas) from Svalbard, Norway. Sci Total Environ 264:267-281.

Corsolini S, Kannan K, Imagawa T, Focardi S, Giesy JP. 2002. Polychloronaphthalenes and other dioxin-like compounds in Arctic and Antarctic marine food webs. Environ Sci Technol 36:3490-3496.

De Guise S, Shaw SD, Barclay JS, Brock J, Brouwer A, Dewailly E, et al. 2001. Consensus statement: Atlantic Coast Contaminants Workshop 2000. Environ Health Perspect 109:1301-1302.

De Wit CA. 2002. An overview of brominated flame retardants in the environment. Chemosphere chemosphere: see atmosphere.  48:583-624.

Dewailly E, Mulvad G, Pedersen HS, Ayotte P., Demers A, Weber JP, et al. 1999. Concentration of organochlorines organochlorines

see chlorinated hydrocarbons.


organochlorines poisoning
cause excitement and irritability, tremor, ataxia, weakness, paralysis, convulsions.
 in human brain, liver, and adipose tissue autopsy samples from Greenland. Environ Health Perspect 107:823-828.

Giesy JP, Kannan K. 2001. Global distribution of perfluorooctane sulfonate in wildlife. Environ Sci Technol 35:1339-1342.

Haave M, Ropstad E, Derocher AE, Lie E, Dahl E, Wiig O, et al. 2003. Polychlorinated biphenyls and reproductive hormones in female polar bears at Svalbard. Environ Health Perspect 111:431-436. doi:10.1289/ehp.5553 [Online 21 November 2002].

Jacobson JL, Jacobson SW. 2002. Breast-feeding and gender as moderators of teratogenic effects on cognitive development. Neurotoxicol Teratology teratology /ter·a·tol·o·gy/ (ter?ah-tol´ah-je) that division of embryology and pathology dealing with abnormal development and the production of congenital anomalies.teratolog´ic

ter·a·tol·o·gy
n.
 24:349-358.

Kaiser J, Enserink M. 2000. Environmental toxicology. Treaty takes a POP at the dirty dozen. Science 290:2053.

Martineau D, Lemberger K, Dallaire A, Labelle P, Lipscomb TP, Michel P, et al. 2002. Cancer in wildlife, a case study: beluga from the St. Lawrence Estuary, Quebec, Canada. Environ Health Perspect 110:285-292.

Matthiessen P, Law RJ. 2002. Contaminants and their effects on estuarine and coastal organisms in the United Kingdom in the late twentieth century. Environ Pollut 120:739-747.

Norstrom RJ, Belikov SE, Born EW, Garner GW, Malone B, Olpinski S, et al. 1998. Chlorinated chlorinated /chlo·ri·nat·ed/ (klor´i-nat?ed) treated or charged with chlorine.

chlorinated

charged with chlorine.


chlorinated acids
some, e.g.
 hydrocarbon contaminants in polar bears from eastern Russia, North America, Greenland, and Svalbard: biomonitoring of Arctic pollution. Arch Envirn Contam Toxicol 35:354-367.

Skaare JU, Larsen HJ, Lie E, Bernhoft A, Derocher AE, Norstrom R, et al. 2002. Ecological risk assessment of persistent organic pollutants in the arctic. Toxicology 181:193-197.

Walkowiak J, Wiener J-A, Fastabend A, Heinzow B, Kramer U, Schmidt E, et al. 2001. Environmental exposure to polychlorinated biphenyls and quality of the home environment: effects on psychodevelopment in early childhood. Lancet 358:1602-1607.

Wibe AE, 2003. Behavioural Effects of Environmental Pollution in Threespine Stickleback stickleback, common name for members of the family Gasterosteidae, small fishes, widely distributed in both fresh- and saltwaters of the Northern Hemisphere. Sticklebacks range from 1 1-2 to 4 in. (3. , Gasterosteus aculeatus L [PhD thesis]. Trondheim, Norway:Norwegian University of Science and Technology The Norwegian University of Science and Technology, known by its Norwegian acronym NTNU (from Norges teknisk-naturvitenskapelige universitet), is located in Trondheim. .
Bjorn Munro Jenssen
Department of Biology
Norwegian University of Science and Technology
Trondheim, Norway
E-mail: bjorn.munro.jenssen@bio.nmu.no


Bjorn Munro Jenssen is a Professor of ecotoxicology The term ecotoxicology was coined by Truhaut in 1969, who defined it as "the branch of toxicology concerned with the study of toxic effects, caused by natural or synthetic pollutants, to the constituents of ecosystems, animal (including human), vegetable and microbial, in an . His research focuses on physiologic, behavioral, and ecological effects of polyhalogenated organic pollutants in a wide range of wildlife species, from amphibians amphibians

members of the animal class Amphibia. Includes frogs, toads, newts, salamanders and cecilians all capable of living on land or in water.
 to polar bears. He particularly focuses on effects related to endocrine disruption.
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Author:Jenssen, Bjorn Munro
Publication:Environmental Health Perspectives
Date:Apr 1, 2003
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