||The neutrality of this section is disputed. (April 2014)|
A polychlorinated biphenyl (PCB; CAS number 1336-36-3 ) is a synthetic organic chemical compound of chlorine attached to biphenyl, which is a molecule composed of two benzene rings. There are 209 configurations of organochlorides with 1 to 10 chlorine atoms. The chemical formula for a PCB is C12H10−xClx. Of the different PCB arrangements and orientations 130 are used commercially.:2
Polychlorinated biphenyls were widely used as dielectric and coolant fluids in electrical apparatus, cutting fluids for machining operations, carbonless copy paper and in heat transfer fluids. Due to PCBs' environmental toxicity and classification as a persistent organic pollutant, PCB production was banned by the United States Congress in 1979 and by the Stockholm Convention on Persistent Organic Pollutants in 2001. According to the U.S. Environmental Protection Agency (EPA), PCBs cause cancer in animals and are probable human carcinogens.
Concerns about the toxicity of PCBs are largely based on compounds within this group that share a structural similarity and toxic mode of action with dioxin. Toxic effects such as endocrine disruption and neurotoxicity are also associated with other compounds within the group. The maximum allowable contaminant level in drinking water in the United States is set at zero, but due to water treatment technologies, a level of 0.5 parts per billion is the de facto level.
- 1 Physical and chemical properties
- 2 Alternative names
- 3 Industrial production and commercial applications
- 4 Environmental transport and transformations
- 5 Health effects
- 6 History
- 7 Pollution due to PCBs
- 8 Regulation
- 9 Containment
- 10 Methods of destruction
- 11 Homologs
- 12 See also
- 13 References
- 14 External links
Physical and chemical properties
PCBs were produced and marketed as mixtures of many congeners. PCB mixtures are characterized by chlorine content. Less-chlorinated PCBs are odorless, tasteless, clear to pale-yellow, viscous liquids, while highly chlorinated mixtures are more viscous and deeper yellow. They are formed by electrophilic chlorination of biphenyl with chlorine gas. PCBs have low water solubilities — 0.0027-0.42 ng/L for Aroclors,[page needed] and low vapor pressures at room temperature, but they have high solubilities in most organic solvents, oils, and fats. They have dielectric constants of 2.5~2.7, very high thermal conductivity,[page needed] high flash points (from 170 to 380 °C)[page needed] and are chemically fairly inert, being extremely resistant to oxidation, reduction, addition, elimination, and electrophilic substitution. The density varies from 1.182 to 1.566 kg/L.[page needed] Other physical and chemical properties vary widely across the class. As the degree of chlorination increases, melting point and lipophilicity increase, and vapour pressure and water solubility decrease.[page needed]
PCBs readily penetrate skin, PVC (polyvinyl chloride), and latex (natural rubber). PCB-resistant materials include Viton, polyethylene, polyvinyl acetate (PVA), polytetrafluoroethylene (PTFE), butyl rubber, nitrile rubber, and Neoprene.
PCBs resistance to oxidize and reduce in the natural environment makes them very stable compounds, not decomposing readily. They have a long half life (8 to 15 years) and are insoluble in water, which contributes to their stability. Their destruction by chemical, thermal, and biochemical processes is extremely difficult, and presents the risk of generating extremely toxic dibenzodioxins and dibenzofurans through partial oxidation. Intentional degradation as a treatment of unwanted PCBs generally requires high heat or catalysis (see Methods of destruction below).
Structure and toxicity
Toxic effects vary depending on the specific PCB. In terms of their structure and toxicity, PCBs fall into 2 distinct categories, referred to as coplanar or non-ortho-substituted arene substitution patterns and noncoplanar or ortho-substituted congeners.
- Coplanar or non-ortho
The coplanar group members have a fairly rigid structure, with their two phenyl rings in the same plane. It renders their structure similar to polychlorinated dibenzo-p-dioxins (PCDDs) and polychlorinated dibenzofurans, and allows them to act like PCDD's, as an agonist of the aryl hydrocarbon receptor (AhR) in organisms. They are considered as contributors to overall dioxin toxicity, and the term dioxins and dioxin-like compounds is often used interchangeably when the environmental and toxic impact of these compounds is considered.
Noncoplanar PCBs, with chlorine atoms at the ortho positions cause neurotoxic and immunotoxic effects, but at levels much higher than normally associated with dioxins. They do not activate the AhR, and are not considered part of the dioxin group, and as of 1998 had been of less concern to regulatory bodies.[medical citation needed]
Di-ortho-substituted, non-coplanar PCBs interfere with intracellular signal transduction dependent on calcium which may lead to neurotoxicity. In 2000 it was shown that ortho-PCBs can disrupt thyroid hormone transport by binding to transthyretin.
The only North American producer, Monsanto Company, marketed PCBs under the trade name Aroclor from 1930 to 1977. These were sold under trade names followed by a 4-digit number. In general, the first two digits refer to the number of carbon atoms in the biphenyl skeleton (for PCBs this is 12); the second two numbers indicate the percentage of chlorine by mass in the mixture. Thus, Aroclor 1260 has 12 carbon atoms and contains 60% chlorine by mass. An exception is Aroclor 1016, which also has 12 carbon atoms, but has 42% chlorine by mass. Aroclor 1016 was prepared by the fractional distillation of Aroclor 1242, which excluded the higher boiling (i.e., more highly chlorinated) congeners.
Different Aroclors were used at different times and for different applications. In electrical equipment manufacturing in the USA, Aroclor 1260 and Aroclor 1254 were the main mixtures used before 1950; Aroclor 1242 was the main mixture used in the 1950s and 1960s until it was phased out in 1971 and replaced by Aroclor 1016.[page needed]
Industrial production and commercial applications
Estimates have put the total global production of PCBs on the order of 1.5 million tons. The United States was the single largest producer with over 600,000 tons produced between 1930 and 1977. The European region follows with nearly 450,000 tons through 1984. It is unlikely that a full inventory of global PCB production will ever be accurately tallied, as there were factories in Poland, East Germany, and Austria that produced unknown amounts of PCBs.
PCB's commercial utility was based largely on their chemical stability, including low flammability, and physical properties, including electrical insulating properties. PCBs were used as coolants and insulating fluids (transformer oil) for transformers and capacitors, such as those used in old fluorescent light ballasts. PCBs were also used as plasticizers in paints and cements, stabilizing additives in flexible PVC coatings of electrical cables and electronic components, pesticide extenders, cutting oils, reactive flame retardants, lubricating oils, hydraulic fluids, and sealants for caulking in schools and commercial buildings, adhesives, wood floor finishes, such as Fabulon and other products of Halowax in the U.S., de-dusting agents, waterproofing compounds, casting agents, vacuum pump fluids, fixatives in microscopy, surgical implants, and in carbonless copy ("NCR") paper.[page needed] Because of its use as a plasticizer in paints and especially "coal tars" that were used widely to coat water tanks, bridges and other infrastructure pieces, it is recommended that before removing the coal tar by sandblasting it should be tested first to see if PCBs are present.
Aroclor 1254 is routinely used to induce rat liver S9 for mutagenicity tests in biomedical research.
Environmental transport and transformations
PCBs entered the environment through both use and disposal. The environmental transport of PCBs is complex and nearly global in scale.PCBs chemical and physical stability has been responsible for their continuing persistenc.[page needed]
The hydrosphere is the main reservoir. The immense volume of water in the oceans is still capable of dissolving a significant quantity of PCBs.
A small volume of PCBs has been detected throughout the earth's atmosphere. The atmosphere serves as the primary route for global transport of PCBs, particularly for those congeners with one to four chlorine atoms. In the atmosphere, PCBs may be degraded by hydroxyl radicals, or directly by photolysis of carbon-chlorine bonds (even if this is a less important process).
Atmospheric concentrations of PCBs tend to be lowest in rural areas, where they are typically in the picogram per cubic meter range, higher in suburban and urban areas, and highest in city centres, where they can reach 1 ng/m³ or more. In Milwaukee, an atmospheric concentration of 1.9 ng/m³ has been measured, and this source alone was estimated to account for 120 kg/year of PCBs entering Lake Michigan. In 2008, concentrations as high as 35 ng/m³, 10 times higher than the EPA guideline limit of 3.4 ng/m³, have been documented inside some houses in the U.S.
Volatilization of PCBs in soil was thought to be the primary source of PCBs in the atmosphere, but research suggests ventilation of PCB-contaminated indoor air from buildings is the primary source of PCB contamination in the atmosphere.
In biosphere, PCBs can be degraded by either bacteria or eukaryotes, but the speed of the reaction depends on both the number and the disposition of chlorine atoms in the molecule: less substituted, meta- or para- substituted PCBs undergo biodegradation faster than more substituted congeners.
The toxicity of PCBs varies considerably among congeners. The coplanar PCBs, known as nonortho PCBs because they are not substituted at the ring positions ortho to (next to) the other ring, (i.e. PCBs 77, 126, 169, etc.), tend to have dioxin-like properties, and generally are among the most toxic congeners. Because PCBs are almost invariably found in complex mixtures, the concept of toxic equivalency factors (TEFs) has been developed to facilitate risk assessment and regulation, where more toxic PCB congeners are assigned higher TEF values on a scale from 0 to 1. One of the most toxic compounds known, 2,3,7,8-tetrachlorodibenzo[p]dioxin, a PCDD, is assigned a TEF of 1.
Exposure and excretion
In general individuals are exposed to PCBs overwhelmingly through food, much less so by breathing contaminated air, and least by skin contact. Once exposed, some PCBs may change to other chemicals inside the body. These chemicals or unchanged PCBs can be excreted in feces or may remain in a person's body for years, with half lives estimated at 10-15 years. PCBs collect in body fat and milk fat. PCB's biomagnify up the food web and are present in fish and waterfowl of contaminated aquifers. Infants are exposed to PCBs through breast milk or by intrauterine exposure through transplacental transfer of PCBs  and are at the top of the food chain.:249ff
Signs and symptoms
The most commonly observed health effects in people exposed to extremely high levels of PCBs are skin conditions, such as chloracne and rashes, but these were known to be symptoms of acute systemic poisoning dating back to 1922. Studies in workers exposed to PCBs have shown changes in blood and urine that may indicate liver damage. In Japan in 1968, 280 kg of PCB-contaminated rice bran oil was used as chicken feed, resulting in a mass poisoning, known as Yushō disease, in over 1800 people. Common symptoms included dermal and ocular lesions, irregular menstrual cycles and lowered immune responses. Other symptoms included fatigue, headaches, coughs, and unusual skin sores. Additionally, in children, there were reports of poor cognitive development.
There is evidence that crash dieters that have been exposed to PCBs have an elevated risk of health complications. Stored PCBs in the adipose tissue becomes mobilized into the blood when individuals begin to crash diet. PCBs have shown toxic and mutagenic effects by interfering with hormones in the body. PCBs, depending on the specific congener, have been shown to both inhibit and imitate estradiol, the main sex hormone in females. Imitation of the estrogen compound can feed estrogen-dependent breast cancer cells, and possibly cause other cancers, such as uterine or cervical. Inhibition of estradiol can lead to serious developmental problems for both males and females, including sexual, skeletal, and mental development issues.
High PCB levels in adults have been shown to result in reduced levels of the thyroid hormone triiodothyronine, which affects almost every physiological process in the body, including growth and development, metabolism, body temperature, and heart rate. It also resulted in reduced immunity and increased thyroid disorders.
Animals that eat PCB-contaminated food even for short periods of time suffer liver damage and may die. In 1968 in Japan, 400,000 birds died after eating poultry feed that was contaminated with PCBs. Animals that ingest smaller amounts of PCBs in food over several weeks or months develop various health effects, including anemia; acne-like skin conditions (chloracne); liver, stomach, and thyroid gland injuries (including hepatocarcinoma),, and thymocyte apoptosis. Other effects of PCBs in animals include changes in the immune system, behavioral alterations, and impaired reproduction. PCBs that have dioxin-like activity are known to cause a variety of teratogenic effects in animals. Exposure to PCBs causes hearing loss and symptoms similar to hypothyroidism in rats.
||The neutrality of this section is disputed. (April 2014)|
In 2013, the International Agency for Research on Cancer (IARC) classified PCBs as human carcinogens. According to the EPA, PCBs have been shown to cause cancer in animals and evidence supports a cancer-causing effect in humans. Per EPA, studies have found increases in malignant melanoma and rare liver cancers in PCB workers.
As of 2012, a review has shown an association between elevated blood levels of PCBs and non-Hodgkin lymphoma. while studies of PCB workers showed no increased death rates from non-Hodgkin Lymphoma. In 2013, the International Association for Research on Cancer (IARC) determined that the evidence for PCBs causing non-Hodgkin Lymphoma is "limited" and "not consistent".
PCBs may play a role in the development of cancers of the immune system because some tests of laboratory animals subjected to very high doses of PCBs have shown effects on the animals' immune system, and some studies of human populations have reported an association between environmental levels of PCBs and immune response.
In 1865 the first "PCB-like" chemical was discovered, and was found to be a byproduct of coal tar. Years later in 1881, German chemists synthesized the first PCB in a laboratory. Between then and 1914,[dubious ] large amounts of PCBs were released into the environment, to the extent that there are still measurable amounts of PCBs in feathers of birds currently held in museums.[better source needed]
In 1929, Monsanto Chemical Company (now Solutia Inc) took over commercial production of PCBs from Swann Chemical Company. PCBs, originally termed "chlorinated diphenyls", were commercially produced as mixtures of isomers at different degrees of chlorination. The electric industry used PCBs as a non-flammable replacement for mineral oil to cool and insulate industrial transformers and capacitors. PCBs were also commonly used as heat stabilizer in cables and electronic components to enhance the heat and fire resistance of PVC.[dead link]
In the 1930's, the toxicity associated with PCBs and other chlorinated hydrocarbons, including polychlorinated naphthalenes, was recognized due to a variety of industrial incidents. Between 1936 and 1937, there were several medical cases and papers released on the possible link between PCBs and its detrimental health effects. In 1936 a U.S. Public Health Service official described the wife and child of a worker from the Monsanto Industrial Chemical Company who exhibited blackheads and pustules on their skin. The official attributed these symptoms to contact with the worker's clothing after he returned from work. In 1937, a conference about the hazards was organized at Harvard School of Public Health, and a number of publications referring to the toxicity of various chlorinated hydrocarbons were published before 1940. In 1947 Robert Brown reminded chemists that Arochlors were "objectionably toxic. Thus the maximum permissible concentration for an 8-hr. day is 1 mg/m3 of air. They also produce a serious and disfiguring dermatitis".
Through the 1960s Monsanto Chemical Company knew increasingly more about PCB's harmful effects on humans and the environment, per internal leaked documents released in 2002, yet PCB manufacture and use continued with few restraints until the 1970s.
In 1966, PCBs were determined by Swedish chemist Dr. Soren Jensen to be an environmental contaminant. Jensen, according to a 1994 article in Sierra, named chemicals PCBs, which previously, had simply been called "phenols" or referred to by various trade names, such as Aroclor, Kennechlor, Pyrenol, Chlorinol and others.
In the early 1970s, Ward B. Stone of the New York State Department of Environmental Conservation (NYSDEC) first published his findings that PCBs were leaking from transformers and had contaminated the soil at the bottom of utility poles.
PCBs continue to be allowed in "totally enclosed uses" such as capacitors, insulating fluids in transformers and capacitors, vacuum pump fluids, hydraulic fluid. These can in certain failure modes or out-of-specification conditions, leak, catch fire, or explode. Use continues in closed systems such as capacitors and transformers.
The public, legal, and scientific concerns about PCBs arose from research indicating they are likely carcinogens having the potential to adversely impact the environment and, therefore, undesirable as commercial products. Despite active research spanning five decades, extensive regulatory actions, and an effective ban on their production since the 1970s, PCBs still persist in the environment and remain a focus of attention.[page needed]
Pollution due to PCBs
In 1999, the Dioxin Affair occurred when 50 kg of PCB transformer oils were added to a stock of recycled fat used for the production of 500 tonnes of animal feed, eventually affecting around 2,500 farms in several countries. The name Dioxin Affair was coined from early misdiagnosis of dioxins as the primary contaminants, when in fact they turned out to be a relatively small part of the contamination caused by thermal reactions of PCBs. The PCB congener pattern suggested the contamination was from a mixture of Aroclor 1260 & 1254. Over 9 million chickens, and 60,000 pigs were destroyed due to the contamination. The extent of human health effects has been debated, in part due to the use of differing risk assessment methods. One group predicted increased cancer rates, and increased rates of neurological problems in those exposed as neonates. A second study suggested carcinogenic effects were unlikely and that the primary risk would be associated with developmental effects due to exposure in pregnancy and neonates. Two businessmen who knowingly sold the contaminated feed ingredient received two-year suspended sentences for their role in the crisis.
The Italian company Caffaro, located in Brescia, specialized in producing PCBs from 1938 to 1984, following the acquisition of the exclusive rights to use the patent in Italy from Monsanto. The pollution resulting from this factory and the case of Anniston, in the USA, are the largest known cases in the world of PCB contamination in water and soil, in terms of the amount of toxic substance dispersed, size of the area contaminated, number of people involved and duration of production.
The values reported by the local health authority (ASL) of Brescia since 1999 are 5,000 times above the limits set by Ministerial Decree 471/1999 (levels for residential areas, 0.001 mg/kg). As a result of this and other investigations, in June 2001, a complaint of an environmental disaster was presented to the Public Prosecutor's Office of Brescia. Research on the adult population of Brescia showed that residents of some urban areas, former workers of the plant, and consumers of contaminated food, have PCB levels in their bodies that are in many cases 10-20 times higher than reference values in comparable general populations.[medical citation needed] PCBs entered the human food supply by animals grazing on contaminated pastures near the factory, especially in local veal mostly eaten by farmers' families. The exposed population showed an elevated risk of Non-Hodgkin lymphoma, but not for other specific cancers.
In Okinawa, high levels of PCB contamination in soil on Kadena Air Base were reported in 1987 at thousands of parts per million, some of the highest levels found in any pollution site in the world.
Republic of Ireland
In December 2008, a number of Irish news sources reported testing had revealed "extremely high" levels of dioxins, by toxic equivalent, in pork products, ranging from 80 to 200 times the EU's upper safe limit of 1.5 pg WHO-TEQDFP/μg i.e. 0.12 to 0.3 parts per billion.
Brendan Smith, the Minister for Agriculture, Fisheries and Food, stated the pork contamination was caused by PCB-contaminated feed that was used on 9 of Ireland's 400 pig farms, and only one feed supplier was involved. Smith added that 38 beef farms also used the same contaminated feed, but those farms were quickly isolated and no contaminated beef entered the food chain. While the contamination was limited to just 9 pig farms, the Irish government requested the immediate withdrawal and disposal of all pork-containing products produced in Ireland and purchased since 1 September 2008. This request for withdrawal of pork products was confirmed in a press release by the Food Safety Authority of Ireland on December 6.
It is thought that the incident resulted from the contamination of fuel oil used in a drying burner at a single feed processor, with PCBs. The resulting combustion produced a highly toxic mixture of PCBs, dioxins and furans, which was included in the feed produced and subsequently fed to a large number of pigs.
The chemical plant Chemko in Strážske (east Slovakia) was an important producer of polychlorinated biphenyls for the former communist block (Comecon) until 1984. Chemko contaminated a large part of east Slovakia, especially the sediments of the Laborec river and reservoir Zemplínska šírava.
Monsanto manufactured PCBs at its chemical plant in Newport, South Wales, until the mid- to late-1970s. During this period, waste matter, including PCBs, from the Newport site was dumped at a disused quarry near Groes-faen, west of Cardiff, from where it continues to be released in waste water discharges.
PCBs (manufactured through most of the 20th century) originating from Monsanto Chemical Company in Anniston, Alabama (Fort McClellan) were dumped into Snow Creek, which then spread to Choccolocco Creek, then Logan Martin Lake. In the early 2000s, class action lawsuits (led, in at least one case, by the late Johnnie Cochran) were settled by local land owners, including those on Logan Martin Lake, and Lay Reservoir (downstream on the Coosa River), for the PCB pollution. Military personnel residing and training at Fort McClellan were not notified of these dangers and were not a party to the settlement.
In 2007, the highest pollution levels remained concentrated in Snow and Choccolocco Creeks. Concentrations in fish have declined and continue to decline over time; sediment disturbance, however, can resuspend the PCBs from the sediment back into the water column and food web.
In 1976 environmentalists found PCBs in the sludge at Waukegan Harbor, the southwest end of Lake Michigan. They were able to trace the source of the PCBs back to the Outboard Marine Corporation that was producing boat motors next to the harbor. By 1982, the Outboard Marine Corporation was court-ordered to release quantitative data referring to their PCB waste released. The data stated that from 1954 they released 100,000 tons of PCB into the environment, and that the sludge contained PCBs in concentrations as high as 50%.
Late during the construction of new on- and off-ramps in the M-13 interchange on the Zilwaukee bridge approach, workers uncovered an uncharted landfill containing PCB-contaminated waste, necessitating an environmental cleanup. In August 22, 1989, The Detroit Free Press noted that the clean up costs would cost over $100,000 and delay the opening of the ramps to the M-13 interchange in Zilwaukee, which were scheduled for opening that year.
Much of the Great Lakes area were still heavily polluted with PCBs in 1988, despite extensive remediation work. Locally caught fresh water fish and shellfish are contaminated with PCBs, and their consumption is restricted.
From the late 1950s through 1977, Westinghouse Electric used PCBs in the manufacture of capacitors in its Bloomington, Indiana plant. Reject capacitors were hauled and dumped in area salvage yards and landfills, including Bennett's Dump, Neal's Landfill and Lemon Lane Landfill. Workers also dumped PCB oil down factory drains, which contaminated the city sewage treatment plant. The City of Bloomington gave away the sludge to area farmers and gardeners, creating anywhere from 200 to 2000 sites, which remain unaddressed. Over 2 million pounds of PCBs were estimated to have been dumped in Monroe and Owen counties. Although federal and state authorities have been working on the sites' environmental remediation, many areas remain contaminated. Concerns have been raised regarding the removal of PCBs from the karst limestone topography, and regarding the possible disposal options. To date, the Westinghouse Bloomington PCB Superfund site case does not have a Remedial Investigation/Feasibility Study (RI/FS) and Record of Decision (ROD), although Westinghouse signed a US Department of Justice Consent Decree in 1985. The 1985 consent decree required Westinghouse to construct an incinerator that would incinerate PCB-contaminated materials. Due to public opposition to the incinerator, however, the State of Indiana passed a number of laws that delayed and blocked its construction. The parties to the consent decree began to explore alternative remedies in 1994 for six of the main PCB contaminated sites in the consent decree. Hundreds of sites remain unaddressed as of 2014. Monroe County will never be PCB-free, as noted in a 2014 Indiana University program about the local contamination.
On 15 February 2008, Monroe County approved a plan to clean up the three remaining contaminated sites in the City of Bloomington, at a cost of $9.6 million to CBS Corp., the successor of Westinghouse. In 1999, Viacom bought CBS, so they are current responsible party for the PCB sites.
Pittsfield, in western Massachusetts, was home to the General Electric (GE) transformer and capacitor divisions, and electrical generating equipment built and repaired in Pittsfield powered the electrical utility grid throughout the nation. PCB-contaminated oil routinely migrated from GE's 254-acre (1.03 km2) industrial plant located in the very center of the city to the surrounding groundwater, nearby Silver Lake, and to the Housatonic River, which flows through Massachusetts, Connecticut, and down to Long Island Sound. PCB-containing solid material was widely used as fill, including oxbows of the Housatonic River.
Current Massachusetts drinking water standards for PCBs are 0.0005 mg/L.
The most discussed pollution of the Hudson River is General Electric's contamination of the river with Polychlorinated biphenyls (PCBs) between 1947-77. GE dumped an estimated 1.3 million pounds of PCBs into the Hudson River during these years. This pollution caused a range of harmful effects to wildlife and people who eat fish from the river or drink the water. In response to this contamination, activists protested in various ways. Musician Pete Seeger founded the Hudson River Sloop Clearwater and the Clearwater Festival to draw attention to the problem. The activism led to the site being designated as the nation's largest superfund site. Other kinds of pollution, including mercury contamination and sewage dumping, have caused problems also.
One of the largest deliberate PCB spills in American history occurred in the summer of 1978 when 31,000 gallons of PCB-contaminated oil were illegally sprayed in 3-foot (0.91 m) swaths along the roadsides of some 240 miles (390 km) of North Carolina highway shoulders in 14 counties and at the Fort Bragg Army Base. The crime, known as "the midnight dumpings," occurred over nearly 2 weeks, as drivers of a black-painted tanker truck drove down one side of rural Piedmont highways spraying PCB-laden waste and then up the other side the following night.
Under Governor James B. Hunt, Jr., state officials then erected large, yellow warning signs along the contaminated highways that read: "CAUTION: PCB Chemical Spills Along Highway Shoulders." The illegal dumping is believed to have been motivated by the passing of the Toxic Substances Control Act (TSCA), which became effective on August 2, 1978 and increased the expense of chemical waste disposal.
Within a couple of weeks of the crime, Robert Burns and his sons, Timothy and Randall, were arrested for dumping the PCBs along the roadsides. Burns was a business partner of Robert "Buck" Ward, Jr., of the Ward PCB Transformer Company, in Raleigh. Burns and sons pleaded guilty to state and Federal criminal charages; Burns received a three to five-year prison sentence. Ward was acquitted of state charges in the dumping, but was sentenced to 18 months prison time for violation of TSCA.
Cleanup and disposal of the roadside PCBs generated controversy, as the Governor's plan to pick up the roadside PCBs and to bury them in a landfill in rural Warren County were strongly opposed in 1982 by local residents.
In October 2013, at the request of the South Carolina Department of Health and Environmental Control (SCDHEC), the City of Charlotte, North Carolina decided to stop applying sewage sludge to land while authorities investigated the source of PCB contamination. In February 2014, the City of Charlotte admitted PCBs have entered their sewage treatment centers as well.
After the 2013 SCDHEC had issued emergency regulations[dead link] the City of Charlotte discovered high levels of PCB's entering its sewage waste water treatment plants, where sewage is converted to sewage sludge. The city at first denied it had a problem, then admitted an "event" occurred in February 2014, and in April that the problem had occurred much earlier. The city stated that its very first test with a newly changed test method revealed very high PCB levels in its sewage sludge farm field fertilizer. Due to the widespread use of the contaminated sludge, SCDHEC subsequently issued PCB fish advisories for nearly all streams and rivers bordering farm fields that had been applied with city waste.
From 1955 until 1977, the Sangamo Weston plant in Pickens, SC, used PCBs to manufacture capacitors, and dumped 400,000 pounds of PCB contaminated wastewater into the Twelve Mile Creek. In 1990, the EPA declared the 228 acres (0.92 km2) site of the capacitor plant, its landfills and the polluted watershed, which stretches nearly 1,000 acres (4.0 km2) downstream to Lake Hartwell as a Superfund site. Two dams on the Twelve Mile Creek are to be removed and on Feb. 22, 2011 the first of two dams began to be dismantled. Some contaminated sediment is being removed from the site and hauled away, while other sediment is pumped into a series of settling ponds.
In 2009, the state environmental regulators SCDHEC noted fish species in Lake Wateree contained exceptionally high levels of PCB contamination and posted adviseries that fish from the lake were unsafe to eat.
In 2013, the state environmental regulators issued a rare emergency order, banning all sewage sludge from being land applied or deposited on landfills, as it contained very high levels of PCBs. The problem had not been discovered until thousands of acres of farm land in the state had been contaminated by the hazardous sludge. A criminal investigation to determine the perpetrator of this crime was launched.
As of 2015, several bodies of water in the state of Washington were contaminated with PCBs, including the Columbia River, the Duwamish River, Green Lake, Lake Washington, the Okanogan River, Puget Sound, the Spokane River, the Walla Walla River, the Wenatchee River, and the Yakima River.6 October 2015 A study by Washington State published in 2011 found that the two largest sources of PCB flow into the Spokane River were City of Spokane stormwater (44%), municipal and industrial discharges (20%). PCBs entered the environment through paint, hydraulic fluids, sealants, inks and have been found in river sediment and wild life. Spokane utilities will spend $300 million to prevent PCBs from entering the river in anticipation of a 2017 federal deadline to do so. In August 2015 Spokane joined other U.S cities like San Diego and San Jose, California, and Westport, Massachusetts. in seeking damages from Monsanto.
From 1954 until 1971, the Fox River in Appleton, Wisconsin had PCBs deposited into it from Appleton Paper/NCR, P.H. Gladfelter, Georgia Pacific and other notable local paper manufacturing facilities. The Wisconsin DNR estimates that after wastewater treatment the PCB discharges to the Fox River due to production losses ranged from 81,000 kg to 138,000 kg. (178,572 lbs. to 304,235 lbs). The production of Carbon Copy Paper and its byproducts led to the discharge into the river. Fox River clean up is ongoing. 
In 1973, the use of PCBs in "open" or "dissipative" sources, such as plasticisers in paints and cements, casting agents, fire retardant fabric treatments and heat stabilizing additives for PVC electrical insulation, adhesives, paints and waterproofing, railroad ties was banned in Sweden.
In 1979, concern over the toxicity and persistence (chemical stability) of PCBs in the environment led the United States Congress to ban their domestic production.
In 1981, the UK banned closed uses of PCBs in new equipment, and nearly all UK PCB synthesis ceased; closed uses in existing equipment containing in excess of 5 litres of PCBs were not stopped until December 2000.
|This section does not cite any references or sources. (September 2015)|
Because of its difficult containment, many buildings (at least in the U.S.A.) with known high PCB dangers have been evacuated and shut down. In many states, including California, laws require any building with such dangers to be sealed and locked, with large warning signs on every entrance point indicating a PCB presence and also a notice to indicate the presence of chemicals known to cause cancer, health problems or reproductive harm. Until a safe solution can be well established, many of these buildings remain undemolished and sealed. Some forms of containment other than building closure and lockdown are noted below.
Large quantities of PCBs have been placed in landfills, mainly in the form of transformers and capacitors. Many municipal sites are not designed to contain these pollutants, and thus PCBs are able to escape into the atmosphere or groundwater. No emissions above background are seen if the landfill is designed correctly.
Methods of destruction
These can be separated into three distinct categories: physical, microbial, and chemical destruction.
Incineration – Although PCBs do not ignite themselves, they can be combusted under extreme and carefully controlled conditions. The current regulations require that PCBs are burnt at a temperature of 1200 °C for at least two seconds, in the presence of fuel oil and excess oxygen.[dead link] A lack of oxygen can result in the formation of PCDDs, PCDFs and dioxins, or the incomplete destruction of the PCBs. Such specific conditions mean that it is extremely expensive to destroy PCBs on a tonnage scale, and it can only be used on PCB-containing equipment and contaminated liquid. This method is not suitable for the decontamination of affected soils.
Irradiation – If a deoxygenated mixture of PCBs in isopropanol or mineral oil is subjected to irradiation with gamma rays then the PCBs will be dechlorinated to form biphenyl and inorganic chloride. The reaction works best in isopropanol if potassium hydroxide (caustic potash) is added. Solvated electrons are thought to be responsible for the reaction. If oxygen, nitrous oxide, sulfur hexafluoride, or nitrobenzene is present in the mixture then the reaction rate is reduced. This work has been done recently in the US often with used nuclear fuel as the radiation source.
Pyrolysis – Destruction of PCBs with pyrolysis using plasma arc processes, like incineration, uses heat. However, unlike incineration, there is no combustion. The long-chain molecules are broken with extreme temperature provided by an electric arc in an inert environment. Adequate post-pyrolysis treatment of the resultant products is required in order to prevent the risk of back reactions.
Much recent work has centered on the study of micro-organisms that are able to decompose PCBs. In general, these organisms work in one of two ways: Either they use the PCB as a carbon source or destruction takes place through reductive dechlorination, with the replacement of chlorine with hydrogen on the biphenyl skeleton. However, there are significant problems with this approach. First, these microbes tend to be highly selective in their dechlorination, with lower chlorinated biphenyls being readily transformed, and with preference to dechlorination in the para and meta positions (this is an advantage however, as ortho dechlorination would transform noncoplanar PCBs into dioxin-like coplanar ones). Second, microbial dechlorination tends to be rather slow-acting on PCB as a soil contaminant in comparison to other methods. Last, while microbes work well in laboratory conditions, there is often a problem in transferring a successful laboratory strain to a natural system. This is because the microbes can access other sources of carbon, which they decompose in preference to PCBs. A low voltage current can stimulate the microbial degradation of PCBs.
Enzymes and vitamins extracted from microbes that show PCB activity have been tested for use in biodegradation. Especially promising seems to be the use of vitamin B12, in which a cobalt ion is in oxidation state (III) under normal redox conditions. Using titanium (III) citrate as a strong reductant converts the cobalt from Co(III) to Co(I), giving a new vitamin known as B12s, a powerful nucleophile and reducing catalyst can then be used on PCBs,[where?] which it dechlorinates in a rapid and selective manner. In 2005, Shewanella oneidensis biodegraded a high percent of PCBs in soil samples.
|This section does not cite any references or sources. (September 2015)|
Many chemical methods are available to destroy or reduce the toxicity of PCBs. Nucleophilic aromatic substitution is a method of destroying low-concentration PCB mixtures in oils, such as transformer oil. Substitution of chlorine by polyethylene glycols occurs in under two hours under a blanket of nitrogen, to prevent oxidation of the oil, to produce aryl polyglycols, which are insoluble in the oil and precipitate out.
Between 700 and 925 °C, H2 cleaves the carbon-chlorine bond, and cleaves the biphenyl nucleus into benzene, yielding HCl without a catalyst. This can be performed at lower temperatures with a copper catalyst, and to yield biphenyl. However, since both of these routes require an atmosphere of hydrogen gas and relatively high temperatures, they are prohibitively expensive.
Reaction with highly electropositive metals, or strong reducing agents such as sodium naphthalide, in aprotic solvents results in a transfer of electrons to the PCB, the expulsion of a chloride ion, and a coupling of the PCBs. This is analogous to the Wurtz reaction for coupling halogenoalkanes. The effect is to polymerise many molecules, thereby reducing the volatility, solubility, and toxicity of the mixture. This methodology is most successful on low-strength PCB mixtures and can also be performed electrochemically in a partly aqueous bicontinuous microemulsion.
The solution photochemistry of PCBs is based on the transfer of an electron to a photochemically excited PCB from a species such as an amine, to give a radical anion. This either expels a chloride ion and the resulting aryl radical extracts a hydrogen atom from the solvent or immediately becomes protonated, leading to the loss of a chlorine atom. It is useful only for water-soluble PCBs.
The major pathway for atmospheric destruction of PCBs is via attack by OH radicals. Direct photolysis can occur in the upper atmosphere, but the ultraviolet wavelengths necessary to excite PCBs are shielded from the troposphere by the ozone layer. It has, however, been shown that higher wavelengths of light (> 300 nm) can degrade PCBs in the presence of a photosensitizer, such as acetone.
The Schwartz reaction is the subject of much study, and has significant benefits over other routes. It is advantageous since it proceeds via a reductive process, and thus yields no dioxins through oxidation. The proposed reaction scheme involves the electron transfer from a titanium (III) organometallic species to form a radical anion on the PCB molecule which expels chlorine to eventually form the relatively non-toxic biphenyl.
For a complete list of the 209 PCB congeners, see PCB congener list. Note that biphenyl, while not technically a PCB congener due to its lack of chlorine substituents, is still typically included in the literature.
|PCB Homolog||CASRN||Cl Substituents||Number of Congeners|
|Biphenyl (not a PCB)||92-52-4||0||1|
|Wikimedia Commons has media related to Polychlorinated biphenyls.|
- Bay mud
- Organochlorine compound
- Polybrominated biphenyl
- Zodiac, a novel by Neal Stephenson which involves PCBs and their impact on the environment.
- UNEP Chemicals (1999). Guidelines for the Identification of PCBs and Materials Containing PCBs (PDF) (1). United Nations Environment Programme. p. 40. Retrieved 2007-11-07.
- Robertson, edited by Larry W.; Hansen, Larry G. (2001). PCBs : recent advances in environmental toxicology and health effects. Lexington, Ky.: University Press of Kentucky. p. 11. ISBN 0813122260.
- Porta, M; Zumeta, E (2002). "Implementing the Stockholm Treaty on Persistent Organic Pollutants". Occupational and Environmental Medicine 10 (59): 651–2. doi:10.1136/oem.59.10.651. PMC 1740221. PMID 12356922.
- "Health Effects of PCBs". U.S. Environmental Protection Agency. 13 June 2013.
- "Consumer Factsheet on Polychlorinated Biphenyls" (PDF). National Primary Drinking Water Regulations. U.S. Environmental Protection Agency. May 14, 2009.
- "PCB Transformers and Capacitors from management to Reclassification to Disposal" (pdf). http://www.chem.unep.ch. United Nations Environmental Program. pp. 55, 63. Retrieved 2014-12-30.
- Boate, Amy; Deleersnyder, Greg; Howarth, Jill; Mirabelli, Anita; Peck, Leanne (2004). "Chemistry of PCBs". Retrieved 2007-11-07.[self-published source?]
- Identifying PCB-Containing Capacitors (PDF). Australian and New Zealand Environment and Conservation Council. 1997. pp. 4–5. ISBN 0-642-54507-3. Retrieved 2007-07-07.
- Mahan, Meegan (May 4, 1998). "Are pcbs still a problem in the great lakes?". Archived from the original on July 22, 2012.[self-published source?]
- Safe, Stephen; Hutzinger, Otto (1984). "Polychlorinated Biphenyls (PCBs) and Polybrominated Biphenyls (PBBs): Biochemistry, Toxicology, and Mechanism of Action". Critical Reviews in Toxicology 13 (4): 319–95. doi:10.3109/10408448409023762. PMID 6091997.
- Safe, Stephen; Bandiera, Stelvio; Sawyer, Tom; Robertson, Larry; Safe, Lorna; et al. (1985). "PCBs: Structure-Function Relationships and Mechanism of Action". Environmental Health Perspectives 60: 47–56. doi:10.1289/ehp.856047. JSTOR 3429944. PMC 1568577. PMID 2992927.
- Winneke, Gerhard; Bucholski, Albert; Heinzow, Birger; Krämer, Ursula; Schmidt, Eberhard; et al. (1998). "Developmental neurotoxicity of polychlorinated biphenyls (PCBS): Cognitive and psychomotor functions in 7-month old children". Toxicology Letters. 102-103: 423–8. doi:10.1016/S0378-4274(98)00334-8. PMID 10022290.
- Simon, Ted; Britt, Janice K.; James, Robert C. (2007). "Development of a neurotoxic equivalence scheme of relative potency for assessing the risk of PCB mixtures". Regulatory Toxicology and Pharmacology 48 (2): 148–70. doi:10.1016/j.yrtph.2007.03.005. PMID 17475378.
- Chauhan, K; Kodavanti, PR; McKinney, JD (2000). "Assessing the Role of ortho-Substitution on Polychlorinated Biphenyl Binding to Transthyretin, a Thyroxine Transport Protein". Toxicology and Applied Pharmacology 162 (1): 10–21. doi:10.1006/taap.1999.8826. PMID 10631123.
- "Proceedings of the Subregional Awareness Raising Workshop on Persistent Organic Pollutants (POPs), Bangkok, Thailand". United Nations Environment Programme. 25 November 1997. Retrieved 2007-12-11.
- "Brand names of PCBs — What are PCBs?". Japan Offspring Fund / Center for Marine Environmental Studies (CMES), Ehime University, Japan. 2003. Retrieved 2008-02-11.
- Erickson, Mitchell D.; Kaley, II, Robert G. "Applications of polychlorinated biphenyls" (pdf). Springer-Verlag. Retrieved 2015-03-03.
- Breivik, K; Sweetman, A; Pacyna, J; Jones, K (2002). "Towards a global historical emission inventory for selected PCB congeners — a mass balance approach1. Global production and consumption". The Science of the Total Environment 290 (1–3): 181–98. doi:10.1016/S0048-9697(01)01075-0. PMID 12083709.
- Godish, T. (2001). Indoor environmental quality (1st ed.). Boca Raton, Florida: Lewis Publishers. pp. 110–30.
- Rudel, Ruthann A; Seryak, Liesel M; Brody, Julia G (2008). "PCB-containing wood floor finish is a likely source of elevated PCBs in residents' blood, household air and dust: A case study of exposure". Environmental Health 7: 2. doi:10.1186/1476-069X-7-2. PMC 2267460. PMID 18201376.
- "S9 and Metabolic Activation". Molecular Toxicology, Inc.
- Wethington, David M.; Hornbuckle, Keri C. (2005). "Milwaukee, WI, as a Source of Atmospheric PCBs to Lake Michigan". Environmental Science & Technology 39 (1): 57–63. doi:10.1021/es048902d. PMID 15667075.
- Jamshidi, Arsalan; Hunter, Stuart; Hazrati, Sadegh; Harrad, Stuart (2007). "Concentrations and Chiral Signatures of Polychlorinated Biphenyls in Outdoor and Indoor Air and Soil in a Major U.K. Conurbation". Environmental Science & Technology 41 (7): 2153–8. doi:10.1021/es062218c. PMID 17438756.
- Van den Berg, Martin; Birnbaum, Linda; Bosveld, Albertus T. C.; Brunström, Björn; Cook, Philip; et al. (1998). "Toxic Equivalency Factors (TEFs) for PCBs, PCDDs, PCDFs for Humans and Wildlife". Environmental Health Perspectives 106 (12): 775–92. doi:10.1289/ehp.98106775. JSTOR 3434121. PMC 1533232. PMID 9831538.
- Crinnion, Walter (March 2011). "Polychlorinated Biphenyls: Persistent Pollutants with Immunological, Neurological, and Endocrinological Consequences" (PDF). Environmental Medicine 16 (1): 5. PMID 21438643. Retrieved 1 October 2015.
- "Public Health Statement for Polychlorinated Biphenyls (PCBs)". Toxic Substances Portal. Agency for Toxic Substances and Disease Registry. 3 March 2011. Retrieved 2 October 2015.
- Purdue University, EPA region 5 (n.d.). "Exploring the Great Lakes.BIOACCUMULATION / BIOMAGNIFICATION EFFECTS" (PDF). EPA. p. 2. Retrieved 3 October 2015.
- Sandra Steingraber. Having Faith. An Ecologists journey to motherhood. 2001, Berkley; 350 pages, Chapter 12: The View from the top. ISBN 0425189996
- Aoki, Yasunobu. "Polychlorinated biphenyls, polychloronated dibenzo-p-dioxins, and polychlorinated dibenzofurans as endocrine disrupters—what we have learned from Yusho disease." Environmental research 86.1 (2001): 2-11.
- Aoki, Y (2001). "Polychlorinated Biphenyls, Polychloronated Dibenzo-p-dioxins, and Polychlorinated Dibenzofurans as Endocrine Disrupters—What We Have Learned from Yusho Disease". Environmental Research 86 (1): 2–11. doi:10.1006/enrs.2001.4244. PMID 11386736.
- Disease ID 8326 at NIH's Office of Rare Diseases
- PCB Baby Studies Part 2
- Environmental Diseases from A to Z
- Jacobson, J. L. and Jacobson, S. W. (1996). Intellectual Impairment in Children Exposed to Polychlorinated Biphenyls in Utero. New England Journal of Medicine, 335(11): 783-789.
- Johnson, B. L. et al (1999). Public Health Implications of Exposure to Polychlorinated Biphenyls (PCBs). Agency for Toxic Substances and Disease Registry.
- Stewart, P. et al 2000. Prenatal PCB exposure and neonatal behavioral assessment scale (NBAS) performance. Neurotoxicology and Teratology, 22: 21-29.
- Agency for Toxic Substances and Disease Registry, CDC. (2000, September 1). Pcbs: toxicity treatment and management. Retrieved from http://www.atsdr.cdc.gov/csem/csem.asp?csem=22&po=10
- Hagmar L, Rylander L, Dyremark E, et al. Plasma concentrations of persistent organochlorines in relation to thyrotropin and thyroid hormone levels in women. Int Arch Occup Environ Health 2001;74:184-188.
- "Contamination of rice bran oil with PCB used as the heating medium by leakage through penetration holes at the heating coil tube in deodorization chamber". Hatamura Institute for the Advancement of Technology. Retrieved 2007-12-11.
- Goldey, E.S.; Kehn, L.S.; Lau, C.; Rehnberg, G.L.; Crofton, K.M. (November 1995). "Developmental Exposure to Polychlorinated Biphenyls (Aroclor 1254) Reduces Circulating Thyroid Hormone Concentrations and Causes Hearing Deficits in Rats". Toxicology and Applied Pharmacology 135 (1): 77. doi:10.1006/taap.1995.1210.
- Lauby-Secretan, B; Loomis D, Grosse Y, El Ghissassi F, Bouvard V, Benbrahim-Tallaa L, Guha N, Baan R, Mattock H, Straif K on behalf of the International Agency for Research on Cancer Monograph Working Group (2013). "Carcinogenicity of polychlorinated biphenyls and polybrominated biphenyls". Lancet Oncology 14: 287–288. doi:10.1016/s1470-2045(13)70104-9. PMID 23499544.
- Kramer, Shira; Hikel, Stephanie Moller; Adams, Kristen; Hinds, David; Moon, Katherine (2012). "Current Status of the Epidemiologic Evidence Linking Polychlorinated Biphenyls and Non-Hodgkin Lymphoma, and the Role of Immune Dysregulation". Environmental Health Perspectives 120 (8): 1067–75. doi:10.1289/ehp.1104652. PMC 3440083. PMID 22552995.
- Kimbrough, R. D.; M. L. Doemland; J. S. Mandel (2003). "A mortality update of male and female capacitor workers exposed to polychlorinated biphenyls". Journal of Occupational and Environmental Medicine 3 (45): 271–282.
- Riseborough, Robert; Brodine, Virginia (1971). "More Letters in the Wind". In Novick, Sheldon; Cottrell, Dorothy. Our world in peril: an Environment review. Greenwich, Conn.: Fawcett. pp. 243–55.
- Karlyn Black Kaley, Jim Carlisle, David Siegel, Julio Salinas (October 2006). Health Concerns and Environmental Issues with PVC-Containing Building Materials in Green Buildings (pdf). Integrated Waste Management Board, California Environmental Protection Agency, USA. p. 11. Retrieved 2007-08-03.
- Drinker, C.K., M.F. Warren, and G.A. Bennet (1937). "The problem of possible systemic effects from certain chlorinated hydrocarbons". Journal of Industrial Hygiene and Toxicology 19 (7): 283–311.
- Butler, David A. (2005). "Connections: The Early History of Scientific and Medical Research on 'Agent Orange'" (PDF). Journal of Law and Policy 13 (2): 527–42.
- Brown, R. M. (1947). "The toxicity of the 'Arochlors'". Chemist-Analyst 36: 33.
- "Monsanto Hid Decades Of Pollution; PCBs Drenched Ala. Town, But No One Was Ever Told," The Washington Post, January 1, 2002 Tuesday, A SECTION; Pg. A01, 4567 words, Michael Grunwald, Washington Post Staff Writer
- S. Jensen (1966). "Report of a new chemical hazard". New Sci. 32: 612.
- Eric FrancisSUNY Dorms Test Toxic. Independent sample indicates PCBs remain in residence hall called clean Woodstock Times, Vol. 23, No. 29; July 21, 1994
- Bernard A, Broeckaert F, De Poorter G, De Cock A, Hermans C, Saegerman C, Houins G (2002). "The Belgian PCB/dioxin incident: analysis of the food chain contamination and health risk evaluation". Environ. Res. 88 (1): 1–18. doi:10.1006/enrs.2001.4274. PMID 11896663.
- Covaci A, Voorspoels S, Schepens P, Jorens P, Blust R, Neels H (2008). "The Belgian PCB/dioxin crisis-8 years later An overview". Environ. Toxicol. Pharmacol. 25 (2): 164–70. doi:10.1016/j.etap.2007.10.003. PMID 21783853.
- Dioxin scandal: 2 year suspended prison sentence Expatica, 5 Feb 2009
- Turrio-Baldassarri, Luigi; et al. (2008). "PCDD/F and PCB in human serum of differently exposed population groups of an Italian city". Chemosphere 73 (1): S228–S234. PMID 18514762.
- La Rocca C, Mantovani A (2006). "From environment to food: the case of PCB". Annali-Istituto Superiore di Sanita 42 (4): 410. PMID 17361063.
- Zani C, Toninelli G, Filisetti B, Donato F (2013). "Polychlorinated biphenyls and cancer: an epidemiological assessment". Journal of Environmental Science and Health, Part C: Environmental Carcinogenesis and Ecotoxicology Reviews 31 (2): 99–144. doi:10.1080/10590501.2013.782174. PMID 23672403.
- U.S. military report suggests cover-up over toxic pollution in Okinawa Jon Mitchell, Japan Times, 17 March 2014
- "Food body to meet on pork recall". BBC (BBC). 7 December 2008. Retrieved 27 October 2014.
- "COMMISSION REGULATION (EC) No 1881/2006setting maximum levels for certain contaminants in foodstuffs". ial Journal of the European. 9 December 2006. Retrieved 27 October 2014.
- "Firm at centre of toxin scare investigated". RTE news. 9 December 2008. Retrieved 27 October 2014.
- "Q&A: The recall of Irish pork". BBC. 2008-12-07. Retrieved 2008-12-08.
- "Recall of Pork and Bacon Products December 2008" (Press release). Food Safety Authority of Ireland. December 2008. Retrieved 27 May 2013.
- "Report of the Inter-Agency Review Group on the Dioxin Contamination Incident in Ireland in December 2008" (PDF). Department of Agriculture, Food & the Marine. Dec 2009.
- Himič, Dan (2009). "Viete, čo doma dýchate?" [Do you know what you breathe at home?]. Život (in Slovak) (33).
- "Chemko Strážske" (in Slovak). Greenpeace. Archived from the original on May 16, 2011.
- Levitt, Tom (21 February 2011). "Monsanto agrees to clean up toxic chemicals in South Wales quarry". The Guardian. Retrieved 16 September 2013.
- US EPA: "Anniston PCB Site"
- Rypel, Andrew L.; Findlay, Robert H.; Mitchell, Justin B.; Bayne, David R. (2007). "Variations in PCB concentrations between genders of six warmwater fish species in Lake Logan Martin, Alabama, USA". Chemosphere 68 (9): 1707–15. doi:10.1016/j.chemosphere.2007.03.046. PMID 17490714.
- Ashworth, William (1987). The Late, Great Lakes. Wayne State University Press. ISBN 978-0-8143-1887-4.[page needed]
- Mahan, Meegan L. (May 4, 1998). "Are PCBs still a problem in the great lakes?". Archived from the original on July 22, 2012.[self-published source?]
- Christopher J. Bessert. "Michigan Highways: In Depth: The Zilwaukee Bridge". michiganhighways.org.
- Hileman, Bette (February 8, 1988). "Great Lakes Cleanup Effort". Chemical and Engineering News 66 (6): 22–39. doi:10.1021/cen-v066n006.p022.
- "Ohio Sport Fish Consumption Advisory" (PDF).
- "US EPA Region 5 Superfund". Retrieved 2009-09-01.
- "Westinghouse/ABB Plant Facility". 2006. Retrieved 2010-02-24.
- "Monroe Co. approves PCB clean up". IndyStar.com. Archived from the original on 2008-02-18. Retrieved 2008-02-18.
- "GE/Housatonic River Site in New England: Site History and Description". USEPA. Retrieved 18 July 2010.
- "Find New England Sites - NEW BEDFORD SITE". epa.gov.
- "New Bedford Harbor, MA - Northeast Region - DARRP". noaa.gov.
- West, C. (1997). Massachusetts drinking water standards and guidelines. Retrieved from Department of Environmental Protection website: http://www.hopkinton.org/water/pdf/97dws.pdf , retrieved 12/30/2013
- "Hudson River PCBs — Background and Site Information". United States Environmental Protection Agency. Retrieved 2007-12-31.
- "Clearwater News and Bulletins". Retrieved 22 September 2015.
- Harrington, Gerry (2014-01-31). "Movement afoot to name bridge after Pete Seeger". United Press International. Retrieved 2014-02-03.
- Levinton, J.S.; Ochron, S.T.P. (2008). "Temporal and geographic trends in mercury concentrations in muscle tissue in five species of hudson river, USA, fish". Environmental Toxicology and Chemistry 27 (8): 1691–1697. doi:10.1897/07-438.1. PMID 18266478.
- New York State Department of Environmental Conservation (NYSDEC). Albany, NY. (2007). "Hudson River Estuary Program: Cleaning the river: Improving water quality" (PDF). p. 24. Archived from the original (PDF) on 2008-02-27. Retrieved 2007-12-31.
- "Carolinians Angry Over PCB Landfill". NY Times. 11 August 1982.
- Charlotte-Mecklenburg Utilities Advisory Committee (October 17, 2013). "Charlotte-Mecklenburg Utilities Advisory Committee Minutes" (PDF). p. 3.
- "Task force named to probe chemical dumping". Charlotte Observer. 7 February 2014.
- http://www.scdhec.gov/administration/news/2013/nr20130925-01.htm. Missing or empty
- "More PCBs found in Charlotte wastewater, city says". Charlotte Observer. 4 April 2014.
- South Carolina Department of Health and Environmental Control. (July 3, 2014). "DHEC Releases Safe Fish Eating Advisory for S.C. Waters". http://www.scdhec.gov/Agency/NewsReleases/2014/nr20140703-01/.
- Sangamo Weston, Inc./Twelve-Mile Creek/Lake Hartwell PCB Contamination, USEPA
- Dam Demolition Begins On Twelve Mile River, WYFF News 4, February 22, 2011.
- "DHEC: General Agency Information". scdhec.gov. 2013.
- Washington State Department of Health Fish Consumption Advisories Fish Consumption Advisories,Page accessed August 8, 2015
- State of Washington Department of Ecology. April 2011. Spokane River PCB Source Assessment: 2003-2007
- Nicholas Deshais (3 August 2015). "Spokane sues Monsanto for PCB contamination". The Spokesman-Review. Retrieved 14 August 2015.
- Associated Press (August 3, 2015). "Spokane sues Monsanto over Spokane River contamination". Seattle Times. Retrieved 14 August 2015.
- "Basic Information". Polychlorinated Biphenyls (PCBs). US EPA.
- "Guidance on municipal waste strategies, Section 5.12 Equipment, which contains low volumes of PCBs" (PDF). UK Department of the Environment, Transport and the Regions. 2001. p. 17. Retrieved 2008-01-29.
- [dead link] "Polychlorinated Biphenyl Inspection Manual" Check
|url=scheme (help) (PDF). US EPA. Aug 2004.
- Mincher, B.J.; Arbon, R.E.; Meikrantz, D.H. (1 September 1992). "High energy decomposition of halogenated hydrocarbons. FY 1992 final report". Energy Citations Database. US Sept of Energy, Office of Science and Technical Information.
- US 6132561, Mincher, Bruce J.; Randy Dale Curry & Thomas E. Clevenger et al., "Process for the solvent extraction for the radiolysis and dehalogenation of halogenated organic compounds in soils, sludges, sediments and slurries", published 9 Oct 1998, issued 17 Oct 2000
- Chun CL; Payne RB; Sowers KR; May HD (January 2003). "Electrical stimulation of microbial PCB degradation in sediment". Water Research 47: 141–152. doi:10.1016/j.watres.2012.09.038. PMID 23123087.
- Woods, Sandra L.; Trobaugh, Darin J.; Carter, Kim J. (1999). "Polychlorinated Biphenyl Reductive Dechlorination by Vitamin B12s: Thermodynamics and Regiospecificity". Environmental Science & Technology 33 (6): 857. doi:10.1021/es9804823.
- De Windt W, Aelterman P, Verstraete W. (2005). "Bioreductive deposition of palladium (0) nanoparticles on Shewanella oneidensis with catalytic activity towards reductive dechlorination of polychlorinated biphenyls.". Environmental Microbiology 7 (3): 314–25. doi:10.1111/j.1462-2920.2005.00696.x. PMID 15683392.
- ATSDR Toxicological Profile U.S. Department of Health and Human Services
- IARC PCB Monograph
- US EPA PCB Homepage
- National Toxicology Program technical reports searched for "PCB"
- Polychlorinated Byphenyls: Human Health Aspects by the WHO
- Case study of plasma arc process for the destruction of PCBs
- Current Intelligence Bulletin 7: Polychlorinated (PCBs)—NIOSH/CDC (1975)
- It's Your Health - PCBs (Health Canada)
- Introduction to Capacitors oil-filled