Document q3a4RE2Kv095ngdQE1gG20g5k

I I :s of the s(CITCE). lodui: idge. England 1BOCKRIS ylvania, USA ute of Switzerland RYSSELBERGHE USA ENS/ img papers on och year, imicaActa thus iut the rapidly limlca Acta: :ossos oloctrodes ont valoncy states octrodcs in , :tion copy MEV 11/69 I I Water Research Pcrgamon Press 1970. Vol. 4, pp. 265-269. Primed in Grc.nl Britain A REVIEW OF CHLORINATED BIPHENYL CONTAMINATION IN NATURAL WATERS Gilman D. Vlitii and G. Frld Llc Water Chemistry Laboratory University of Wisconsin, Madison, Wis. 53706, U.S.A. (Received 10 Not ember 1969) Abstract--A review of the present slate of knowledge concerning environmental contamina tion by organochlorine compounds indicates that the chlorinated biphenyls may be one of the more widespread contaminants. The significance of this contamination has not yet been evaluated due, in part, to the lack of systematic analytical procedures for the quantitative and qualitative determinations of flic components of chlorinated biphenyl mixtures. The possibility of the chlorinated biphenyls producing serious errors in chlorinated pesticide analyses is emphasized. INTRODUCTION Chemical determinations of the types and concentrations of chlorinated pesticides in natural waters have become increasingly important to fish management, wildlife ecology, and water pollution control. Based on gas chromatographic (GLC) analyses of environmental samples, pp'DDE is generally considered to be one of the more widespread contaminants. How-, ver, implicit in every GLC analysis is the possibility that unresolved and/or unidentified components which have specific retention volumes similar to that of the desired substance may introduce serious errors in the interpreta tion of the chromatogram. Increasing numbers of investigators have reported the presence of organochlorine compounds in environmental samples which cannot be identified as the common chlorinated pesticides. Although the unidentified compounds have been attributed from presumptive evidence to the metabolites of common pesticides, plasticizers, or chlorinated biphenyls, proper chemical identifications have not been reported. Therefore, when studying natural water systems wliich receive industrial wastes, it may be more correct to consider unidentified compounds as chlorinated organic contaminants until confirmation techniques are developed. Within the last three years, the chlorinated biphenyls (or polychlorinated biphenylsPCB) have received considerable study. The preliminary evidence indicates that this group of organochlorine compounds may be widespread in the environment. For example, Widmark (1967) reported that mass-spectrum analyses of compounds eluting from GLC of fish and bird extracts indicated that unknown organochlorine compounds were present which behaved as chlorinated biphenyls of higher chlorine content. More recently, mass numbers and chlorine numbers per molecule for each peak in the chromatograph of commerical chlorinated biphenyl were reported (Jensen et a!., 1968). However, to our knowledge, no spectral data or other confirm atory data for positive structural identification of these compounds have ever been published. With this improper basis of identification, a number of other publications have followed which identify unknown compounds as chlorinated biphenyls. Since mixtures of chlorinated biphenyls may contain greater than 20 compounds which can only be 4WATCH /+-- 265 mm* DSW 033731 STLCOPCB4017693 266 Gilman D. Vi mi and G. Fiild Lee resolved by Gl.C with great difficulty, assignment of unidentified peaks to one of the chlorinated biphenyls has been accomplished by comparison of a chlorinated biphenyl with (he nearest relative retention time. For example, Holden and Marsden (1967), who had earlier reported the presence of unknown compounds in fish (IIolden, 1966), reported the presence of chlorinated biphenyls in seals witluto supporting data other than relative retention data from GLC columns. RoniNSON ct al. (1967) reported compounds of unknown identity in marine organisms which gave GLC retention times longer than pp'DDE and microcoulometric response. The authors indicated that the chromatographic characteristics of the unknowns suggested they were not metabolites of the "cyclodicnc-type" pesticides as lias been proposed by Ro'.iurn (1965). Holmes et al. (1967) attributed unknown peaks from GLC to the chlorinated biphenyls and noted that the substances seemed to accumulate in organisms associated with natural waters (seals, fish and birds) to a greater extent than in domestic animals. This work reported relative rentention data with no supporting data. Risedrough ct al. (1968 a) and Riserrough et al. (1968 b) reported organochlorinc compounds in fish, birds and bird eggs which were attributed to the chlorinated biphenyls. With no supporting data and despite the absence of structural confirmations for the chlorinated biphenyls, the investigators reported concentrations of the unknowns (as chlorinated biphenyls) as well as ratios of DDT to chlorinated biphenyls. From these ratios, it was concluded that a chlorinated biphenyl fallout pattern existed around industrial centers and that air transport of the contaminants was significant. Koeman et al. (1969) presented GLC chromatograms of extracts from environ mental samples as well as mass numbers and numbers of chlorine atoms per molecule for each peak of the chromatogram. Although no spectral data were presented, the mass number data strongly suggested that chlorinated biphenyls were present. This paper also presented the results of the analyses for each unknown as being "present" or "absent" in a particular sample, rather than attempting to quantitate the amount of material present. THE CHLORINATED BIPHENYLS Since contamination of the environment by chlorinated biphenyls has been impli cated in the brief review presented, the need for the environmental scientist to become familiar with the present state of knowledge concerning these molecules is apparent. Mixtures of chlorinated biphenyls have been manufactured since 1929 and present registered trademarks for commercial brands include: Arochlor (Monsanto), Chlorcxtol (Allis-Chalmcrs), Dykanol (Corncll-Dubilicr Division, Federal Pacific Electric), lncrtcen (Wcstinghousc), Nofiamol (Wagner Electric), Pyramol (G. E.), Thcrmiuol (Monsanto) in the U.S.; and Clophen (I. G. Farbenidustrie A. G., Ger many), Fcnclor (Cafiaro, Italy), Kanncchlor (Kancgafuchi Chemical Co., Japan), Pyralcne (Prodclcc, France), and Soval (Russia) (Huddard, 1964). The chlorinated biphenyls have been used as plasticizers for adhesives, polyvinyl acetates, acrylic resins, in scaling compounds, pipe joint compounds, printing ink, rubber manufactur ing, high pressure-high temperature lubricants, fungicidal insulations, anti-corrosion, nail coatings, water proofings, diffusion pump fluid, stabilization of polymers, dielectrics, preventing (Monsanto et al., 1955) The toxic has not be indicate tha "safe'' is t.( highly chic with chlon reported rc\ biphenyls ( effects of A cited) to tl 5460 to be More ret. biphenyls o tion, and t factor of b dicldrin ;in- However with organ possibility biological i review of t other meta enzyme im great as pp facts make cules have conccntrat Some co studies of o biphenyl. I analyses. 11 have been i make the ; of chcmica For cx.l step which residues (1 was treatc It was cor. nitration s m ipuynnf mi m. i 'HMM i?"1 mm it * wifmi DSW 033732 STLCOPCB4017694 >nc Of ||)C biphniyl N (1067), N, 1966), ala oilier i marine to nilorisitcs of icsticidcs orinalcd sociatcd animals. chlorine urinated malions of the irinated fallout ninants nvironolcculc cd, the t. Tin's resent" mount impli'cconic went, 'resent into), 'nciftc . I:.), Gcrpnn), ta led rylic :turion, ters, A Review of Chlorinated Uiphcnyl Contamination in Natural Water? 267 dielectrics, heat transfer media, coax-cab!c insulations, paints and varnishes, ice preventing coatings, and is an evaporation retardant for pesticide applications (Monsanto O/I'L-306; Huihiaro, 1964; Hopkins and Hoffman, 1955; Sullivan eta!., 1955). The toxicity and sublethal effects of the chlorinated biphenyls to biological systems has not been thoroughly evaluated (Rr.tcnn., 1969). Inhalation tests on animals indicate that maximum concentrations of chlorinated biphenyls as vapor which are "safe" is 1.0 mg/m3 for the lower chlorinated biphenyls and 0.5 mg/m3 for the more highly chlorinated biphenyls (Hubbard, 1964), Continuous or repeated skin contact with chlorinated biphenyl leads to a condition called "chloracnc" which has been reported repeatedly with industrial workers handling products containing chlorinated biphenyls (Mligs et al., 1953). Sullivan and Hornstlin (1953) found no toxic effects of Arochlor 5460 on Hies, but the chlorinated terphcnyls were toxic (no levels cited) to the elm leaf beetle (Duda, 1957). Dlonilr et at. (1946) found Arochlor 5460 to be non-toxic at 0.1 ppm (24 hr) to the larvae of Anopheles quadrimacutatus. More recently, Lichtenstein et al. (1969) reported the toxicity of the chlorinated biphenyls to houseflies (D. melanogaster) decreased with increasing degree of chlorina tion, and that the chlorinated biphenyls appear to be less toxic than dicldrin by a factor of 1000. The chlorinated biphenyls were found to increase the toxic effect of dicldrin and DDT on houseflies. However, in addition to investigating the sources of environmental contamination with organochlorine compounds, the environmental scientist is concerned with the possibility that these organochlorine molecules may exhibit detrimental effects on biological communities at snblctha! levels. Kupfer (1967) has presented an extensive review of the clfccls of chlorinated pesticides on steroid hydroxylase induction and other metabolic systems. Also, Risebrougm et at. (1968 b) have demonstrated that enzyme induction by the chlorinated biphenyls (Arochlor 1262) was five times as great as pp'DDE or technical DDT as determined via ocstradiol degradation. These facts make tolerance limits set by bioassay less significant since organochlorine mole cules have the capacity to produce physiological effects in organisms at sublethal concentrations. ANALYTICAL PROCEDURES Some controversy has been generated over the analytical procedures utilized in studies of organochlorine contaminants which have been attributed to the chlorinated biphenyl. In general, the procedures arc similar to typical chlorinated pesticide analyses. However, chemical reactions such as dchydrohalogcnalion and nitration have been introduced prior to electron capture gas chromatography in attempts to make the procedures more selective for the chlorinated biphenyls. It is the addition of chemical treatment steps which has caused disagreement in the literature. For example, after extract clean up, Jensen and Widmark (1967) used a nitration step which is similar to that used in removing DDT and metabolites from toxaphcnc residues (Euro et al., 1967; Kawano et al., 1969). Briefly, the concentrated extract was treated with a mixture of If2SO and IiNOj (cone, 1:1, v/v) at 0C for 5 min. It was concluded incorrectly that only PCB and BHC isomers arc unaffected by the nitration step. Risebrough et al. (1969) have reported the use of similar procedures. \ yi m* !> HwpiJinnM '!) DSW 033733 i STLCOPCB4017695 268 Gilman D. Vditii and G. Fred Llk To the contrary, Reynolds (1969) has been unable to repeat the nitration step rcproducibly for a number of reasons. First, the reaction is not specific for (lie PCD and BHC isomers, since hcptachlor epoxide remains unaffected by nitration. Also, the work of Bevenue (Frro, 1967; Kawano, 1969) has demonstrated that toxaphenc, lhe reaction product of the chlorination of camphcnc which produces in excess of 20 unresolved peaks on GLC, is apparently unaltered by nitration. Second, Reynolds found some loss of the earlier eluting chlorinated biphenyls during nitration. Third, and most significant, peaks with longer retention volumes appeared in the chromato grams after nitration. These peaks resulted from the nitration of other aromatic mole cules in the mixture because nitro groups reduce the vapor pressures in the gas phase (GLC) and the aromatic nitro grouping has a high affinity for the secondary electrons in the electron capture detector. Results of studies of this laboratory (Venn and Lle, 1969) have substantiated earlier reports (Degurse, 1969) that fish and natural waters in several areas of Wisconsin contain unidentified organochlorine contaminants. Using essentially the same pro cedures discussed by Reynolds (1969), the resulting chromatograms contain many peaks which have retention volumes similar to those of components of several com mercial chlorinated biphenyl mixtures. However, components with corresponding retention volumes were also observed in chromatograms of technical chlordanc, hcptachlor epoxide, benzene hexachloridc, and toxaphenc, as well as analytical standards of a number of the DDT family of pesticides. Accordingly, qualitative and quantitative interpretations of such chromatograms from Wisconsin fish and water await more detailed and systematic investigations of the extracts. CONCLUSIONS The preliminary evidence of the past several years, which has been reviewed in this communication, indicates that the environment associated with natural waters is becoming contaminated with unidentified organochlorine compounds from unknown sources. The facts that chlorinated biphenyls have been strongly implicated as con taminants, that the chlorinated biphenyls have been widely used in industry and have been prepared commercially since 1929, and that the mixtures produce GLC peaks with retention volumes similar to common chlorinated pesticides create a need for basic studies concerning analytical procedures for chlorinated hydrocarbons. Also, it is apparent that comprehensive and systematic investigations into the chemistry and the physiological effects of the contaminants as well as the degree and sources of the contamination are essential before control measures can be considered. Uotni n A. 216. 12 HolmisD ' An tare How-s 1 MunnAnn I Chemii JfNSIN S-. Dccoir Jenstn S : Scplcc Kawano 5 mine Chem. Kor.MAN fish, n 221, I Kuphr r> boloii Licutenst be i A-c Meigs J. v J. Am Monsant< RflC.IIII. ' Wild! Reynolds an.ily RisfnRuut ` alt,in ; RiSEuaeo* I chtor ; RlSEDROU' j polyc Robinson , chtor Rodurn- i ions; I and I ; Sullivan I flics < ! Sullivan ! outd : Verm G. | Repo WlDMAXX REFERENCES Dcgursc P. (1969) Personal communication from the Wisconsin Department of Natural Resources, Madison. , Deonicr C. C., Jones H. A. and Incho H. H. (1946) Organic compounds effective against larvae of Anopheles quadrimaculattis. J. econ. Ent. 39, 459-462. Duda J. (1957) The use of chlorinated polyphenyls to increase the effective insecticidal life of lindane. /. econ. Ent. 50, 218-219. Erro E., Revenue A. nnd Beckman H. (1967) A method for the determination of toxaphenc in the presence of DDT. Dull. Environ. Contam. Toxicol. 2, 372-379. Holden A. V. (1966) Organochlorine insecticide residues in Salmonid fish. J. appl. Econ. 3,45-53. mpu ii!iwwws!iwi mu* "I ann i \ DSW 033734 STLCOPCB4017696 aitration step : for the PCI) ion. Also, ll>c Txaplicnc, tlie excess of 20 ut, Reynolds alion. Third, ic chromatoom.iiic tnolc:hc i'as phase ary electrons dinted earlier if Wisconsin c same proantain many several coinirrcsponding I chlordane, s analytical dilative and h and water reviewed in al waters is ; ti unknown I ted as con i 7 and have | 3LC peaks a need for ions. Also, i miistry and ; rccs of the I Resources, ist larvae of i of lindane. Iicnc in (he 3, 45-53. A Review of Chlorinated Biphenyl Contamination in Natural Waters 260 HoLnrN A. V. and Marsden K. (1967) Organochlorinc pesticides in seals and porpoises. Nature Lind 216, 1274-1276. 1 Ioi.mi.5 I). C., Simmons J. H. and Tatton J. O'G. (1967) Chlorinated hydrocarbons in British wildlife. Nature, Ixind. 216, 227 -229. HorKtNS T. L. and I Iotfman R. A. (1955) Effectiveness of dilon and certain candidate synergists against 1)DT resistant house flics. J, ecan. Em, 48, 146-147, HunnARD H. 1.. (1964) Chlorinated biphenyl and related compounds. Kirk-Othmer Encyclopedia of Chemical Technology, 2nd cdn. Vol. 5, 289-297. 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(1952) Chloracnc from an unusual exposure to Arochior. J. Am. med. Ass. 154, 1417-1418. Monsanto company, Technical Bulletin O/PL-306, St. Louis, Missouri. Reichel W. L. (1969) Chief, section of Chemistry. Personal communication from the Patuxent Wildlife Research Center, Laurel, Maryland. Reynolds L. M. (1969) Polychlorobiphcnyls (PCB's) and their interference with pesticide residue analysis. Dull. Etw. Contain. Toxical. 4, 128-143. Rislhrougii R. W., Huggf.tt R. J., Gripun J. J. and Goldderg E. D. (1968 a) Pesticides: Trans atlantic movements in the Northeast Trades. Science 159, 1233-1234. Risiiirough R. W., Rilciie P., Herman S. G., Rfakall D. B. and Kirvin M. N. (1968 b) Poly chlorinated biphenyls in the global ecosystem, Nature, Land. 220, 1098-1102. Riserrough R. W,, Rii chi; P. and Olcott H. S. (1969) Current progress in the determination of the polychlorinated biphenyls. Dull. Env. Contain. Toxicol. 4, 192-201. Robinson J., Richardson A., Crabtree A. N., Coulson J. C. and Potts G. R. (1967) Organo- chlorine residues in marine organisms. Nature, Land. 214, 1307-1311. Roourn J. (1965) A simple concentration cell technique for determining small amounts of halide ions and its use in (lie determination of residues of organochlorine pesticides in extracts of animal and plant tissue. Analyst 90, 467-475. Sullivan W. N, and Hornstein I. (1953) A comparison of evaporation rates and toxicity to house flics of lindane and lindane-chlorinated polypheny! deposits. J. econ. Em. 46, 882-894. Suluvan W. N., Hornstein I. nnd Yeomans A. H. (1955) Improved deposits for controlling insects outdoors. J. econ. Ent. 48, 153-155. Veith G. D. and Lee G. F. (1969) Chlorinated Organic Contaminants in the Milwaukee River. Progress Report to the Wisconsin Department of Natural Resources, Madison, October, mimeo. Widmark G, (1967) Pesticide Residues. J. Ass. Official Analyt. Chem. 50,1069. ' /- \ \ \ m* m jin iMejn \ DSW 033735 STLCOPCB4017697