Polychlorinated naphthalene (PCN) products are made by chemically reacting chlorine with naphthalene. There are 75 possible congeners of chlorinated naphthalenes. Commercial products are generally mixtures of several congeners and range from thin liquids to hard waxes to high melting point solids. 
Production of PCNs started in 1910, it peaked between 1930 and 1950. US production decreased from 3200 tonnes in 1957 to about 320 tonnes in 1978 due to the replacement of PCNs by substitutes. By 1980 US production had ceased. PCNs have been mainly used in cable insulation, wood preservation, engine oil additives, electroplating masking compounds, capacitors and as a feedstock for dye production. The major sources of release of PCNs into the environment are likely from waste incineration (which also produces dioxins) and disposal of items containing chlorinated naphthalenes to landfill.
They have a low water solubility, and adsorb to particles, soils and sediments. Highly chlorinated PCNs have a higher tendency to adsorb than those that are less chlorinated. They are stable chemicals although they can be biodegraded in the soil by micro-organisms. Chlorinated naphthalenes have been shown to be highly bioaccumulative in fish, but less so in shrimp and algae. The amount of bioaccumulation observed increases with the degree of chlorination, although the highest chlorinated naphthalenes appear to bioaccumulate less.
PCNs are toxic to marine organisms. Some algae might show a reduced growth at concentrations above 0.1 mg/l. Concentrations of 80 µg/l are toxic for horseshoe crabs, and concentrations of only 20 µg/l might already cause effects on moulting. In work places PCN concentrations up to 14.5 mg/m3 have been measured in work places. These conditions caused severe skin rashes and liver conditions which led to the dead of workers. 
Environmental standards and legislation