Hanspaul Hagenmaier

Input/output balance of estrogenic active compounds in a major municipal sewage plant in Germany

24 h samples of untreated and treated wastewater were taken in parallel from a modern municipal sewage plant in southern Germany in March and June 1998. After solid phase extraction, total estrogenic activity was quantitatively measured with a miniaturized E-screen assay and the levels of nine estrogenic phenolic chemicals analyzed by HRGC/LRMS. 17Beta-estradiol equivalent concentrations (EEQ) were 58 and 70 ng/l in the influent and 6 ng/l in the effluent, indicating that the load of estrogenic activity of the wastewater was reduced by about 90% in the sewage plant. Less than 3% of the estrogenic activity was found in the sludge. 4-t-octylphenol, 4-nonylphenol, bisphenol A, 2-hydroxybiphenyl, and 4-chloro-3-methylphenol were detected in the untreated wastewater at levels from 0.13 to 3.6 microg/l. 4-t-octylphenol, 4-nonylphenol, and bisphenol A were present in the effluent at concentrations from 0.16 to 0.36 microg/l, 2-hydroxybiphenyl and 4-chloro-3-methylphenol were not detectable. The contribution of the quantified levels of phenolic xenoestrogens to total estrogenic activity in the sewage was 0.7-4.3%.

Phenolic xenoestrogens in surface water, sediments, and sewage sludge from Baden-Württemberg, south-west Germany.

Nine structurally different phenolic chemicals, which have been reported to mimic estrogen effects, were determined in various aquatic environmental compartments. Twenty-three water samples from five streams and rivers showed levels up to 458 ng/l for 4-nonylphenol (4NP), 189 ng/l for 4-t-octylphenol (4tOP), 272 ng/l for bisphenol A (BPA) and 47 ng/l for 2-hydroxybiphenyl (2OHBiP). Elevated levels of these compounds in a stream with a high load of effluents of sewage treatment plants (STPs), compared to a brook free of sewage, identified STPs as major sources. With a similar order, 4NP (10-259 micrograms/kg dry matter), 4tOP (< 0.5-8 micrograms/kg), BPA (< 0.5-15 micrograms/kg), and 2OHBiP (2-69 micrograms/kg) were also detected regularly in riverine sediment (n = 11). Levels in sewage sludge were one order of magnitude higher than in sediments. 4-Hydroxybiphenyl and 4-chloro-3-methylphenol were found predominantly in sludge and sediment in the lower ppb range.

Dioxin-like PCBs in the environment - human exposure and the significance of sources

Dioxin-like PCBs represent an important component of the Sigma-TEQ in many environmental media. Specifically, in animal produce and in fish PCBs dominate the Sigma-TEQ ingested by humans. This in turn leads to high background body burdens in humans with PCB-TEQ greater than that associated with PCDD/Fs. High fish consumers are apparently subject to elevated TEQ exposure from dioxin-like PCBs. This has important implications for exposure assessment studies which have previously only been concerned with PCDDs and PCDFs. Unlike PCDD/Fs, dioxin-like PCBs are not controlled within the food chain. Sources and pathways of exposure are poorly defined. Aroclor formulations and their subsequent usage are considered to be the most important sources in terms of human exposure to some TEF-rated congeners, notably PCB-118, PCB-156 and part of PCB-126. Emissions from combustion sources contribute additional PCB-126. More research is needed to place these compounds in an integrated risk evaluation framework.

Low temperature decomposition of PCDD/PCDF, chlorobenzenes and PAHs by TiO2-based V2O5-WO3 catalysts

The oxidation of representative congeners of polychlorinated dibenzo-p-dioxins (PCDDs), polychlorinated dibenzofurans (PCDFs), polychlorinated chlorobenzenes (PCBzs), and of polyaromatic hydrocarbons (PAHs) was investigated on two commercial V2O5–WO3/TiO2-based catalysts, optimized for the combined reduction of nitrogen oxides and decomposition of dioxins. The non-chlorinated polyaromatic compounds (including non-chlorinated dibenzodioxin and dibenzofuran) are destroyed at temperatures as low as 150°C with an efficiency of more than 95%. PCDD and PCDF were also removed from the gas phase with an efficiency of >98%. However, at 150°C they remained mainly unchanged (up to 75%) adsorbed on the catalyst. A decrease in the oxidation rate with increasing chlorine substitution was found for the PCDD/PCDF. This could be explained by an increasing “redox potential” with increasing chlorine substitution due to the electron withdrawing effect of the chlorine. For the more volatile monoaromatic PCBz, however, the effect of lowering the volatility with increasing chlorine substitution (resulting in longer residence time on the catalyst) over-compensates the effect of the increasing “redox potential” with higher degree of chlorination.

Development of a sensitive E-screen assay for quantitative analysis of estrogenic activity in municipal sewage plant effluents

A simplified proliferation test with human estrogen receptor-positive MCF-7 breast cancer cells (E-screen assay) was optimized and validated for the sensitive quantitative determination of total estrogenic activity in effluent samples from municipal sewage plants. After solid phase extraction of 1 l sewage on either 0.2 g polystyrene copolymer (ENV+) or 1 g RP-C18 material and removal of the solvent, analysis of the extracts in the E-screen assay could be performed without any clean-up step. This was even possible with untreated sewage. Parallel extraction of four sewage samples on both different solid phase materials gave comparable quantitative results in the E-screen. A blank sample did not induce cell proliferation. As additive behaviour of the estrogenic response of single compounds was proven for two different mixtures each containing three xenoestrogens, total estrogenic activity in the sewage samples, expressed as 17 beta-estradiol equivalent concentration (EEQ), could be calculated comparing the EC50 values of the samples with those of the positive control 17 beta-estradiol. The detection limit of the E-screen method was 0.05 pmol EEQ/l (0.014 ng EEQ/l), the limit of quantification 0.25-0.5 pmol EEQ/l (0.07-0.14 ng EEQ/l). In total, extracts of nine effluent and one influent sample from five different municipal sewage plants in South Germany were analyzed in the E-screen. All samples strongly induced cell proliferation in a dose-dependent manner which was completely inhibited by coincubation with 5 nM of the estrogen receptor-antagonist ICI 182,780. The proliferative effect relative to the positive control 17 beta-estradiol (RPE) was between 30 and 101%. 17 beta-Estradiol equivalent concentrations were between 2.5 and 25 ng/l indicating a significant input of estrogenic substances via sewage treatment plants into rivers.

Isomerspecific analysis of pentachlorophenol and sodium pentachlorophenate for 2,3,7,8-substituted PCDD and PCDF at sub-ppb levels

Abstract So far analyses of pentachlorophenol (PCP) and sodium pentachlorophenate (PCP-Na) for tetra- and CDD/CDF have been carried out mainly at detection limits of 1 ppb or higher (1–7). We have now analyzed 4 commercial PCP and PCP-Na samples for tetra- and pentaCDD/CDF at detection limits of 0.1 ppb. 2,3,7,8-TCDD was analyzed at a detection limit of less than 0.05 ppb (8). This was achieved by two different procedures. 2,3,7,8-TCDD was selectively separated from other PCDD and PCDF by chromatography on basic alumina (8,9). The separation of tetra- and pentaCDD/CDF from hexa- to octaCDD/CDF was accomplished by reversed phase chromatography. Analyses were carried out isomer specific for the 2,3,7,8-substituted PCDD/PCDF. In the two samples of PCP-Na analyzed 2,3,7,8-TCDD was detected at levels of 0.5 and 0.23 ppb respectively, and 1,2,3,7,8-pentaCDD was found in all four samples in concentrations of 0.19 to 18 ppb. It therefore appears no longer valid to consider 1,2,3,7,8-pentaCDD as a “marker” for PCDD/PCDF originating from combustion sources. In the view of these findings the risk assessment for pentachlorophenol and its salts should be reconsidered.

PCDDs and PCDFs in sewage sludge, river and lake sediments from south west Germany

Sewage sludges and sediments of rivers and lakes are sinks for “persistent” organic compounds entering the environment. These matrices are therefore useful in the assessment of local and global pollution with certain compounds or classes of compounds. In recent years we have analyzed sediments of the rivers Neckar, Rhine, and Danube, from Lake Constance, and samples of sewage sludge from municipal waste water treatment plants of south-west Germany for PAH, phthalates, organochlorine pesticides, and PCBs. 1 We have now analyzed a number of these samples for PCDDs and PCDFs. Isomer-specific analyses for 2,3,7,8-subsituted PCDDs/PCDFs were carried out in all cases. In all samples PCDDs could be detected, and in most cases PCDFs as well. 2,3,7,8-TCDD was never detected at a detection limit of 0.01 ppb. In sediments (14 samples) the total PCDDs ranged from 0.1 to 2.9 ppb and PCDFs from “not detectable” to 1.2 ppb. The highest concentration for a 2,3,7,8-substituted PCDD∗ was found for 1,2,3,6,7,8-hexaCDD with 0.06 ppb. In sewage sludges (15 samples) the total PCDDs ranged from 4 to 65 ppb and PCDFs from 1 to 7 ppb. The highest concentration for a 2,3,7,8-substituted PCDD∗ was found for 1,2,3,6,7,8-hexaCDD with 0.57 ppb. Comparison of PCDD/PCDF patterns of congeners and isomers for the sewage sludge and river sediment samples with those of stack gas emissions of waste incinerators and of pentachlorophenol allows the conclusion that the main source of PCDDs and PCDFs found in these samples is pentachlorophenol. Results of the Lake Constance sediment core indicate that here the atmospheric immission from waste incineration might be predominant.

Correlation of environmental occurrence of polychlorinated dibenzo-p-dioxins and dibenzofurans with possible sources

Abstract A new method for source identification of polychlorinated dibenzo-p-dioxins (PCDD) and polychlorinated dibenzofurans (PCDF) was developed. This method is based on the comparison of the profiles of relative concentrations of 2,3,7,8-substituted PCDD/PCDF congeners. The new procedure is compared with the methods for source identification applied hitherto: comparison of homologue profiles, congener profiles or isomer patterns. Cluster analysis of the relative concentrations of 2,3,7,8-substituted PCDD/PCDF congeners leads to plausible correlations between sources and environmental samples.

Mechanism of the formation of polychlorinated dibenzo-p-dioxins and dibenzofurans from chlorophenols in gas phase reactions

The pyrolysis of chlorinated phenates at a temperature of about 280 degrees C results in the formation of definite chlorinated dibenzodioxin (PCDD) congeners [1-3]. It is shown that in gas phase reactions chlorophenols react in the presence of oxygen above 340 degrees C not only to PCDD but also to chlorinated dibenzofurans (PCDF). The mechanism of this reaction of chlorophenols to PCDD and PCDF was elucidated. In a first step phenoxyradicals are formed which are capable of forming PCDDs and PCDFs. This is confirmed by the oxygen dependency of the reaction. In an argon atmosphere no dimerization of chlorophenols could be observed at 420 degrees C. By the identification of intermediates and by analyzing the PCDF isomers formed from individual chlorophenols the reaction pathway is elucidated. As intermediates in the formation of PCDFs polychlorinated dihydroxybiphenyls (DOHB) were identified. These are most likely formed by the dimerization of two phenoxy radicals at the hydrogen substituted carbons in ortho-positions under simultaneous movement of the hydrogen atoms to the phenolic oxygen PCDDs are formed in the gas phase via ortho-phenoxyphenols (POP) analogous to the pyrolysis of phenates, but due to the radical mechanism in the first condensation step to POPs not only a chlorine atom is capable for substitution but also the hydrogen atoms. The formation of the DOHBs and their condensation to PCDFs and hydroxylated PCDFs as well as the ratio of PCDD to PCDF formed show a strong dependency on the reaction temperature, the substitution pattern of the chlorophenols and the oxygen concentration.

Validation and application of a rapid in vitro assay for assessing the estrogenic potency of halogenated phenolic chemicals

The E-Screen assay serves as an in vitro tool for the detection of estrogenic activity of chemicals and extracts of environmental samples. Based on the induction of proliferation in human estrogen receptor-positive MCF-7 breast cancer cells we could substantially simplify the assay. As one important step of validation we applied the modified assay for testing nine known xenoestrogens. We could confirm the results of other groups assuring the reproducibility of the E-Screen assay. The results provide evidence that the E-Screen assay is suitable for determination of estradiol equivalency factors (EEFs) for environmental estrogens to rank their estrogenic potency relative to the natural estrogen 17 beta-estradiol. Further, we used the optimized proliferation test to screen nine halogenated phenolic compounds for their possible estrogenic potency. Three widely applied chemicals expressed a weak receptor-mediated estrogenic activity: the flame retardant Tetrabromo-Bisphenol-A, the disinfectant 4-chloro-3-methylphenol, and the herbicide educt 4-chloro-2-methylphenol. Their estrogenic potencies were five to six orders of magnitude lower than that of 17 beta-estradiol.