Chlorinated polycyclic aromatic hydrocarbon

Chlorinated polycyclic aromatic hydrocarbon

Chlorinated polycyclic aromatic hydrocarbons (ClPAHs) are a group of compounds comprising polycyclic aromatic hydrocarbons with two or more aromatic rings and one or more chlorine atoms attached to the ring system. ClPAHs can be divided into two groups: chloro-substituted PAHs, which have one or more hydrogen atoms substituted by a chlorine atom, and chloro-added ClPAHs, which have two or more chlorine atoms added to the molecule.[1] They are products of incomplete combustion of organic materials. They have many congeners, and the occurrences and toxicities of the congeners differ.[2] ClPAHs are hydrophobic compounds and their persistence within ecosystems is due to their low water solubility.[3] They are structurally similar to other halogenated hydrocarbons such as polychlorinated dibenzo-p-dioxins (PCDDs), dibenzofurans (PCDFs), and polychlorinated biphenyls (PCBs). ClPAHs in the environment are strongly susceptible to the effects of gas/particle partitioning, seasonal sources, and climatic conditions.[4]


Sources of ClPAHs

Chlorinated polycyclic aromatic hydrocarbons are generated by combustion of organic compounds. ClPAHs enter the environment from a multiplicity of sources and tend to persist in soil and in particulate matter in air. Environmental data and emission sources analysis for ClPAHs reveal that the dominant process of generation is by reaction of PAHs with chlorine in pyrosynthesis.[5] ClPAHs have commonly been detected in tap water, fly ash from an incineration plant for radioactive waste, emissions from coal combustion and municipal waste incineration, automobile exhaust, snow, and urban air.[1] They have also been detected in electronic wastes, workshop-floor dust, vegetation, and surface soil collected from the vicinity of an electronic waste (e-waste) recycling facility and in surface soil from a chemical industrial complex (comprising a coke-oven plant, a coal-fired power plant, and a chlor-alkali plant), and agricultural areas in central and eastern China.[6] In addition, the combustion of polyvinylchloride and plastic wrap made from polyvinylidene chloride result in the production of ClPAHs, suggesting that combustion of organic materials including chlorine is a possible source of environmental pollution.[7]

A specific class of ClPAHs, Polychlorinated naphthalene’s (PCNs), are persistent, bioaccumulative, and toxic contaminants that have been reported to occur in a wide variety of environmental and biological matrixes. ClPAHs with three to five rings have been reported to occur in air from road tunnels, sediment, snow, and kraft pulp mills.[8]

Recently, the occurrence of particulate ClPAHs has been investigated. Results have shown that most particulate ClPAH concentration detected in urban air tended to be high in colder seasons and low in warmer seasons. This study also determined through compositional analysis that relatively low molecular weight ClPAHs dominated in warmer seasons and high molecular weight ClPAHs dominated in colder seasons.[4]


ClPAHs are hybrids of dioxins and PAHs, they are suspected of having similar toxicities.[5] These types of compounds are known to be carcinogenic, mutagenic, and teratogenic. Toxicological studies have shown that some ClPAHs possess greater mutagenicity, aryl-hydorcarbon receptor activity, and dioxin-like toxicity than the corresponding parent PAHs.[2]

The relative potency of three ring ClPAHs was found to increase with increasing degree of chlorination as well as with increasing degree of chlorination. However, the relative potenices of even the most toxic ClPAHs have been found to be 100,000-fold lower than the relative potency of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD).[9] Even though ClPAHs aren’t as toxic as TCDD, it has been determined using recombinant bacterial cells that the toxicities of exposure to ClPAHs based on AhR activity were approximately 30-50 times higher than that of dioxins.[4] ClPAHs demonstrate a high enough toxicity to be a potential health risk to human populations that come into contact with them.

DNA interaction

One of the well-established mechanisms by which chlorinated polycyclic aromatic hydrocarbons can exert their toxic effects is via the function of the aryl hydrocarbon receptor (AhR). The AhR-mediated activities of ClPAHs have been determined by using yeast assay systems. Aryl Hydrocarbon Receptor (AhR) is a cytosolic, ligand-activated transcription receptor. ClPAHs have the ability to bind to and activate the AhR. The biological pathway involves translocation of the activated AhR to the nucleus. In the nucleus, the AhR binds with the AhR nuclear translator protein to form a heterodimer. This process leads to transcriptional modulation of genes, causing adverse changes in cellular processes and function.[10]

Several ClPAHs have been determined to be AhR-active. One such ClPAH, 6-chlorochrysene, has been shown to have a high affinity for the Ah receptor and to be a potent AHH inducer.[11] Therefore, ClPAHs may be toxic to humans, and it is important to better understand their behavior in the environment.

Several ClPAHs have also been found to exhibit mutagenic activity toward Salmonella typhimurium in the Ames assay.[1]


  1. ^ a b c Nilsson, U. L., Oestman, C. E. Chlorinated polycyclic aromatic hydrocarbons: method of analysis and their occurrence in urban air. Environ. Sci. Technol. 1993; 27 (9);1826–1831. doi:10.1021/es00046a010
  2. ^ a b Kitazawa A., Amagai, T., Ohura, T. Temporal Trends and Relationships of Particulate Chlorinated Polycyclic Aromatic Hydrocarbons and Their Parent Compounds in Urban Air. Environ. Sci. Technol. 2006; 40 (15); 4592–4598. doi:10.1021/es0602703
  3. ^ Cerniglia, C. E. Biodegradation of polycyclic aromatic hydrocarbons. Biodegradation. 1992; 3; 351–368.
  4. ^ a b c Ohura, T., Fujima, S., Amagai, T., Shinomiya, M. Chlorinated Polycyclic Aromatic Hydrocarbons in the Atmosphere: Seasonal Levels, Gas-Particle Partitioning, and Origin. Enviro. Sci. Technol. 2008; 42 (9); 3296–3302. doi:10.1021/es703068n
  5. ^ a b Ohura, T. Environmental Behavior, Sources, and Effects of Chlorinated Polycyclic Aromatic Hydrocarbons. The Scientific World. 2007; 7; 372–380. PubMed
  6. ^ Ma, J., Horii, Y., Cheng, J., Wang, W., Wu, Q., Ohura, T., Kannan, K. Chlorinated and Parent Polycyclic Aromatic Hydrocarbons in Environmental Samples from an Electronic Waste Recycling Facility and a Chemical Industrial Complex in China. Enviro. Sci. Technol. 2009; 43 (3); 643–649. doi:10.1021/es802878w
  7. ^ Wang, D., Xu, X., Chu, S., Zhang, D. Analysis and structure prediction of chlorinated polycyclic aromatic hydrocarbons released from combustion of polyvinylchloride. Chemosphere. 2003; 53; 495–503. doi:10.1016/S0045-6535(03)00507-1
  8. ^ Horii, Y., Ok, G., Ohura, T., Kannan K. Occurrence and Profiles of Chlorinated and Brominated Polycyclic Aromatic Hydrocarbons in Waste Incinerators. Environ. Sci. Technol. 2008; 42 (6); 1904–1909. doi:10.1021/es703001f
  9. ^ Horii, Y., Khim, J. S., Higley, E. B., Giesy, J. P., Ohura, T., Kannan K. Relative Potencies of Individual Chlorinated and Brominated Polycyclic Aromatic Hydrocarbons for Induction of Aryl Hydrocarbon Receptor-Mediated Responses. Environ. Sci. Technol. 2009; 43 (6); 2159–2165. doi:10.1021/es8030402
  10. ^ Blackenship, A. L., Kannan, K., Villalobos, S. A., Villeneuve, Daniel L., Falandysz, J., Imagawa T., Jakobsson, E., Giesy, J. P. Relative Potencies of Individual Polychlorinated Naphthalenes and Halowax Mixtures to Induce Ah Receptor-Mediated Responses. Enviro. Sci. Technol. 2000; 34 (15); 3153–3158. doi:10.1021/es9914339
  11. ^ Ohura, T., Kitazawa A., Amagai T., Makino M. Occurrence, Profiles, and Photostabilities of Chlorinated Polycyclic Aromatic Hydrocarbons Associated with Particulates in Urban Air. Environ. Sci. Technol. 2005; 39 (1); 85–91. doi:10.1021/es040433s

Wikimedia Foundation. 2010.

Игры ⚽ Нужен реферат?

Look at other dictionaries:

  • hydrocarbon — hydrocarbonaceous, adj. /huy dreuh kahr beuhn, huy dreuh kahr /, n. any of a class of compounds containing only hydrogen and carbon, as an alkane, methane, CH4, an alkene, ethylene, C2H4, an alkyne, acetylene, C2H2, or an aromatic compound,… …   Universalium

  • Bioremediation — can be defined as any process that uses microorganisms, fungi, green plants or their enzymes to return the natural environment altered by contaminants to its original condition. Bioremediation may be employed to attack specific soil contaminants …   Wikipedia

  • 9,10-Diphenylanthracene — IUPAC name 9,10 Diphenylanthracene …   Wikipedia

  • Creosote — For other uses, see Creosote (disambiguation). Creosote is the portion of chemical products obtained by the distillation of a tar that remains heavier than water, notably useful for its anti septic and preservative properties.[1] It is produced… …   Wikipedia

  • Landfarming — Land Farming is a bioremediation treatment process that is performed in the upper soil zone or in biotreatment cells. Contaminated soils, sediments, or sludges are incorporated into the soil surface and periodically turned over (tilled) to aerate …   Wikipedia

  • poison — poisoner, n. poisonless, adj. poisonlessness, n. /poy zeuhn/, n. 1. a substance with an inherent property that tends to destroy life or impair health. 2. something harmful or pernicious, as to happiness or well being: the poison of slander. 3.… …   Universalium

  • environment — environmental, adj. environmentally, adv. /en vuy reuhn meuhnt, vuy euhrn /, n. 1. the aggregate of surrounding things, conditions, or influences; surroundings; milieu. 2. Ecol. the air, water, minerals, organisms, and all other external factors… …   Universalium

  • Carbonless copy paper — (CCP), non carbon copy paper, or NCR paper is an alternative to carbon paper, used to make a copy of an original, handwritten (or mechanically typed) document without the use of any electronics. The process was invented by chemists Lowell… …   Wikipedia

Share the article and excerpts

Direct link
Do a right-click on the link above
and select “Copy Link”