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Photochemical conversion of chlorinated phenolic substances in aquatic media as studied by AOX and Microtox tests.

Six chlorophenolic substances were photochemically converted by illumination with xenon light. The AOX (adsorbable organic halogens) contents were determined after illumination for various periods. Pure chlorinated phenolic substances were readily detected by AOX. Both adsorbable and non-adsorbable chlorinated products were formed. Chloride analysis indicated that most (if not all) of the non-adsorbable products consisted of chloride ions. Microtox, a bacterial bioluminescence test, was used as a screening test for toxic properties of the photolysis products. Products from 2,4,6-trichlorophenol were more toxic than the original substance. Other compounds tested had less toxic products as measured by their combined effect on the Microtox system. Products of 2,4-dichlorophenol, 2,3,4-trichlorophenol, 4,5,6-trichloroguaiacol and 2,3,4,5-tetrachlorophenol did not seem to contribute to the combined toxic properties after partial photolysis of the parent compound. Pentachlorophenol was converted into products which had substantial effects on the Microtox system.

Chlorides↗

The Pacific eulachon (Thaleichthys pacificus) as a pollution indicator organism in the Fraser River estuary, Vancouver, British Columbia.

Eulachons return to the Fraser River each spring and migrate through the estuary to spawn in freshwater. During this migration they may be subjected to varying water quality conditions due to the discharge of domestic and industrial wastes and land drainage. Fish were captured at five estuarine stations in April 1986 and again at three stations in April/May 1988. The locations were from Steveston, at the river mouth, to Port Mann bridge, 31.0 km upstream, just above saltwater influence. Water samples, whole fish, gonads and pooled livers of both sexes were analyzed separately for selected organochlorine contaminants. Water and tissue samples contained chlorophenols from wood preservation operations and chloroguaiacols from pulp bleaching. Whole fish also contained DDE and DDD, while PCBs were present in some fish gonads in 1986, but not in 1988. With the exception of whole body concentrations of 2,3,4,6-tetrachlorophenol (TeCP), concentrations of pentachlorophenol (PCP), 3,4,5-trichloroguaiacol (3,4,5-TCG), tetrachloroguaiacol (TeCG), DDE and DDD in whole bodies, livers and gonads revealed an increasing trend with distance of the eulachon capture site upstream from the Fraser River mouth. Marked differences occurred in the concentration of contaminants in eulachon livers (for example, levels of 50.8 +/- 42.2 ng g-1 3,4,5-TCG at Steveston, and 446.4 +/- 222.5 ng g-1 at Port Mann). The relatively high lipid content of eulachons suggests them to be potential integrators of low-level contaminants in the Fraser River system. This, and their anadromous life history, recommend them as suitable annual monitors of selected organic compounds.

Animals↗

A source inventory and budget for chlorinated dioxins and furans in the United Kingdom environment.

Polychlorinated dibenzo-p-dioxins (PCDDs) and -furans (PCDFs) are ubiquitous in the environment. This paper estimates the present UK environmental loading of PCDD/Fs in soils, vegetation, air, water and sediments. Greater than 95% of the estimated total PCDD/F loading of 5.7 t in the UK environment is present in surface soils. Annual emissions from known primary sources of PCDDs and PCDFs are estimated. The most important of these include: municipal waste incinerator stack emissions (10.9 kg sigma PCDD/F per annum); industrial (7.7 kg/year) and domestic (5.1 kg/year) combustion of coal; clinical waste incinerators (1.7 kg/year); volatilisation from chlorophenol-treated substrates (1.7 kg/year) and combustion of leaded petrol by motor vehicles (0.7 kg/year). These sources are generally easy to define and reasonably reliable national estimates can be obtained. More difficult to quantify are secondary releases from the large UK stock of pentachlorophenol (PCP) and PCP-treated products, which may represent quantitatively one of the most important sources of total PCDD/Fs to the environment. Estimates of homologue-specific emissions indicate that combustion processes represent a far more significant source of tetra and penta CDD/Fs than do chlorophenols, which in turn constitute a greater source of hepta- and octachlorinated congeners. Direct emission of PCDD/Fs into the atmosphere from combustion processes facilitates their atmospheric transport to remote locations. This, coupled with the diffuse nature of combustion processes, means that the effects of PCDD/F contamination originating from anthropogenic combustion are more widespread than those from the use and disposal of chlorophenols. Contamination from chlorophenols will be more localised, owing to the insignificance of direct atmospheric release pathways for this source. Although there is reasonable agreement between the estimated current annual flux and the present UK environmental loading of PCDDs and PCDFs, a large discrepancy exists between the sum of the annual contributions from primary sources and this annual flux. Whilst the existence of an as yet unidentified source or sources or gross underestimates of known sources cannot be excluded, it is proposed that much of this discrepancy may be accounted for by secondary releases from the use and disposal of chlorophenols and the long-range transport, continued remobilisation and subsequent redeposition of PCDDs and PCDFs already present in the environment. Despite limited evidence for a modest decline in levels of PCDDs and PCDFs in some environmental compartments over the last 20 years, the environmental persistence of these chemicals means that they will remain in the UK environment for the foreseeable future despite recent action to curb primary emissions.

Air Pollutants↗

Toxicity of phenolic compounds in relation to the size of a freshwater fish, Notopterus notopterus (Pallas).

Fish, Notopterus notopterus, in four sizes (4.5 +/- 1.0, 9.0 +/- 1.0, 14.5 +/- 1.2, and 22.6 +/- 1.8 cm in length) were exposed to phenol (P), 2,4-dinitrophenol (DNP), and pentachlorophenol (PCP) separately, and also to their three combinations (PCP + DNP)/P (highly antagonistic), (DNP + P)/PCP (additive), and (P + DNP)/PCP (highly synergistic) to evaluate the effect of fish size on the toxicity of these chemicals separately and in combination. The results reveal that with increased fish size (from 4.5 + 1.0 to 14.5 + 12 cm in length) toxicity of phenolic compounds decreased. On the contrary, the larger size fish (22.6 +/- 1.8 cm in length) was comparatively more susceptible. This indicates that change in fish size does influence the toxicity of phenolic compounds.

Animals↗

Effects of ecotoxicological chemicals on passive plasmalemma permeability in plants.

The measurement of changes of electrical conductivity in the external medium of isolated mesophyll protoplasts of Vicia faba, tissue disks of red beetroot (Beta vulgaris), and intact duckweed plants (Lemna gibba) was used to determine nonspecific electrolyte efflux. This provided rapid screening tests to assess the impact of environmental chemicals on passive membrane permeabilities. The conditions of the tests and their applicability to environmental studies are described in detail. Twenty-five reference chemicals selected by the Bundesminister für Forschung und Technologie (BMFT, FRG) were tested. The sequence of effectiveness of the various substances was similar in the different test systems and appeared to be independent of the organizational level of the plant material. Passive electrolyte efflux was most effectively stimulated by HgCl2, pentachlorophenol (PCP), and sodium dodecylbenzenesulfonate (LAS). The threshold concentrations showing clear stimulation of electrolyte efflux after 3 hr of application with protoplasts and 24 hr with tissue disks were in the vicinity of relevant environmental levels. The tests described allow the detection of effects at least down to concentrations of 0.004 mol m-3 HgCl2, 0.001 mol m-3 PCP, and 0.04 mol m-3 LAS. Other putatively very toxic chemicals were ineffective in these short-term permeability tests.

Biological Transport↗

Testing and evaluating some methods to investigate side effects of environmental chemicals on soil microorganisms.

Some methods of measuring soil biological activities (dehydrogenase activity, short- and long-term respiration, ATP content, nitrogen transformation, and straw decomposition) were used to assess their suitability for testing side effects of environmental chemicals on microbial activities. Reproducibility and, especially, the sensitivity of the methods (and activities) were important. In these investigations, the chemicals Aretit (herbicidal ingredient dinoseb acetate), pentachlorophenol, and sodium dodecyl sulfonate (LAS) were applied at different dosages. The trials were run under laboratory and field conditions to examine agreement between the results. The activities tested varied in their sensitivity to the chemicals. Dehydrogenase activity, short-term respiration, ATP content, and, in some cases, nitrogen transformation were the most sensitive, whereas straw decomposition and long-term respiration needed higher dosages for inhibitory effects. Dinoseb acetate was particularly effective. The effects of all chemicals were strongly modified by the soil type, while temperature and moisture had fewer effects. Inhibitory effects lasted several months under laboratory conditions. Agreement between laboratory and field trials was best with dehydrogenase activity.

Adenosine Triphosphate↗

Comparison of the Microtox test with the 96-hr LC50 test for the harpacticoid Nitocra spinipes.

A comparison between the static 96-hr LC50 test with the brackish water harpacticoid Nitocra spinipes and the Microtox (Beckman Instruments, Inc.) screening method has been done. The relationship between the two bioassays were evaluated for 16 pure and technical chemicals and 11 complex effluents from different types of industries. The correlation between the 96-hr LC50 values for Nitocra and the 5-, 15-, and 30-min effective concentration (EC50) for pure and technical chemicals had R2 values ranging between 0.751 and 0.796. A somewhat better correlation was shown between the two test methods for the complex effluents with R2 values ranging from 0.903 to 0.927. The sensitivity of the two tests for the actual types of samples were found to be in the same order of magnitude. Investigations concerning pretreatments of three chemicals (dibutyl phthalate, 1-octanol, and pentachlorophenol) fairly insoluble in water (less than 1000 mg/liter) have been done. Three solvents, acetone, dimethyl sulfoxide (DMSO), and propylene glycol, were studied with the Microtox system in a low concentration (500 mg/liter). Acetone exerted a slightly stimulatory effect and propylene glycol a slight reduction effect on bacterial luminescence.

Acetone↗

Effects of chlorophenols on isolated class A chloroplasts and thylakoids: a QSAR study.

A series of 22 chlorinated phenols was studied for their effects on photosynthesis of isolated chloroplasts. Each chlorophenol was an uncoupler, but the uncoupling activity depended upon substitution. The di-, tri-, or pentachloro substitution greatly enhanced the uncoupling activity. However, 2,6 substitution was not favorable to the uncoupling activity. Fifty percent uncoupling of photophosphorylations was obtained for concentrations between 4 mM for phenol itself, and 20 microM for pentachlorophenol. The quantitative structure-activity relationship (QSAR) study indicated a good relationship between, on the one hand, steric and electronic parameters, and, on the other hand, the uncoupling activity. In such equations, the A parameter describing ortho-substitution, always presented a negative sign. No good equation could be obtained with only log P and sigma. At concentrations which generally induced uncoupling, the chlorinated phenols inhibited the electron transfer in thylakoids. Di, tri, or penta substitution by chlorine enhanced the inhibition. A good relation appeared between this effect and the steric parameters MR and A. The study of isolated class A chloroplasts demonstrated that the uncoupling and the inhibition of the electron transfer in thylakoids could explain the effect of the chlorophenols on the whole photosynthetic mechanism. The effects of phenols on isolated chloroplasts were compared to those obtained with the same series on mitochondria. To explain the differences between QSAR equations, on the one hand for chloroplasts, and, on the other hand, for mitochondria, we suggested a selective binding of chlorinated phenols to proteins of the biological membranes.

Chlorophenols↗

Subchronic metabolic effects and toxicity of a simulated pulp mill effluent on juvenile lake trout, Salmo trutta m. lacustris.

Juvenile lake trout (Salmo trutta m. lacustris) were exposed for 7 weeks to 0.05X and 0.2X 96-hr LC50 concentrations of simulated bleached kraft pulp mill effluent (KME - Sa + CP). A sulfate soap preparation, composed mainly of resin and fatty acids, with added chlorophenols (CP, tri-, tetra-, and penta-CP) was used as the toxicant mixture. Concentrations of free CP in plasma and free and conjugated CP in bile were proportional to their concentrations in the water. The greatest total gradient between bile and water CP was 5.2 X 10(4) for pentachlorophenol. The activity of a liver polysubstrate monooxygenase (PSMO) system, assayed with three model substrates, increased 40 to 67% due to KME - Sa + CP. However, the increase was not directly dependent on the exposure concentration. In contrast to PSMO, activities of conjugating enzymes (p-nitrophenol UDP-glucuronosyl and glutathione transferases) were decreased in the liver. Increased concentration of glutathione was noted in the liver and kidney. In addition, a small (9%) but significant decrease in blood hemoglobin concentration was observed at the higher exposure concentration. Although growth rate of lake trout was markedly decreased due to KME - Sa + CP, hydromineral balance and carbohydrate metabolism in fish were unaffected, indicating possible physiological compensation. On the other hand, lethality tests with lake trout preexposed to KME - Sa + CP at 0.2 X LC50 revealed decreased tolerance, whereas at the lower exposure concentration it was unchanged. We therefore conclude that various physiological adjustments in trout during subchronic exposures were not adaptive in terms of short-term tolerance.

7-Alkoxycoumarin O-Dealkylase↗

Toxicity and bioaccumulation of chlorophenols in earthworms, in relation to bioavailability in soil.

The acute toxicity of five chlorophenols for two earthworm species was determined in two sandy soils differing in organic matter content and the results were compared with adsorption data. Adsorption increased with increasing organic matter content of the soils, but for tetra- and pentachlorophenol was also influenced by soil pH. Earthworm toxicity was significantly higher in the soil with a low level of organic matter. This difference disappeared when LC50 values were recalculated to concentrations in soil solution using adsorption data. Eisenia fetida andrei showed LC50 values lower than those of Lumbricus rubellus although bioaccumulation was generally higher in the latter species. Toxicity and bioaccumulation based on soil solution concentrations increased with increasing lipophilicity of the chlorophenols. The present results indicate that the toxicity and bioaccumulation and therefore the bioavailability of chlorophenols in soil to earthworms are dependent on the concentration in soil solution and can be predicted on the basis of adsorption data. Both the toxicity of and bioaccumulation data on chlorophenols in earthworms demonstrated surprisingly good agreement with those on chlorophenols in fish.

Adsorption↗

Uncoupling properties of a chlorophenol series on Acer cell suspensions: a QSAR study.

A series of 22 chlorinated phenols was investigated for their uncoupling effect on Acer cell suspensions. All the studied molecules were able to enter the cell and had instantaneous uncoupling properties: pentachlorophenol was the best uncoupler of the series (the concentration required to uncouple by 50% was 5 microM), being 200-fold more effective than 3-Cl or 2-Cl phenol, which were the molecules having the lowest activity. The QSAR (quantitative structure-activity relationship) study gave good equations for the uncoupling activity with the steric and electronic parameters taken together. The electronic parameter sigma was always present with a positive sign, whereas A, the angular parameter, was always negative. The general steric parameters (sigma D, 1 chi v, MR) represented the third component of the equations and each of them played practically an equivalent role. Equations of quality (r greater than 0.9), which were statistically significant, could be obtained after four compounds in F (2,5-diCl phenol; 2,4,5-triCl phenol; 2,4-diCl 6-NO2 phenol; and 2-Cl 4,6-diNO2 phenol) had been excluded and when quadratic terms were not present. The best equation (r = 0.940) was obtained with sigma D, A, and sigma 1. The comparison of the significant equations with those previously established with isolated mitochondria led us to suppose that there were no selective limiting steps during the transfer of the studied compounds from the reaction medium to mitochondria inside the cells. The major difference between the uncoupling results obtained with isolated mitochondria and with cells was that the concentrations needed to uncouple by 50% were always higher in cells.

Cells, Cultured↗

A review of the genetic toxicology of chlorinated dibenzo-p-dioxins.

Information from both published and unpublished sources considered relevant to the understanding of the genetic toxicology of chlorinated dibenzo-p-dioxins is summarized in this review. Interest in writing this paper was stimulated by the fact that this class of compounds, particularly 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), has gained notoriety as an extreme environmental and industrial hazard. The potential for human exposure occurs in the work place when dioxins are formed during the synthesis of a number of commercially important compounds such as 2,4,5-trichlorophenoxyacetic acid, hexachlorophene, and pentachlorophenol. Environmental contamination may result from manufacturing processes and from dioxin contaminants in marketed products. Research on dioxins as potential mutagens was initiated because of their structural similarity to acridines, a class of known intercalating agents. To date, only 4 dioxin compounds have been evaluated for mutagenicity: the di-, tetra-, and octa-chlorinated derivatives and the unsubstituted dibenzo-p-dioxin. Since only a few of the many possible structural forms of dioxins have been tested, no definite conclusions can be made about their potential mutagenicity. Furthermore, the positive mutagenicity and cytological effects reported thus far with the few dioxin isomers examined seems to depend on the position of chlorine substitution. The most active form of the molecule is the 2,3,7,8-derivative (TCDD). Data available for assessing the mutagenic potential of TCDD are conflicting and scarce. Differences in testing results reported in these studies could be attributed to solubility problems with the test chemical, treatment protocols, purity of test samples, or toxicity. Because there are conflicting data, additional experiments are needed before the mutagenic potential of TCDD and other dioxins can be determined. Studies exploring the promoting effect of dioxins on the mutagenicity of other compounds are also recommended because experiments have shown TCDD to be an extremely active liver enzyme inducing agent that enhances the mutagenicity of certain polycyclic hydrocarbons such as 3-methylcholanthrene in vitro. The importance of discerning the hazards to human health from dioxin compounds became apparent after an accidental release of TCDD from a chemical plant contaminated the Seveso, Italy area in July 1976. This accident revealed that insufficient data were available to properly evaluate the long-term health risks posed by dioxin compounds. Several research projects were therefore initiated after the Seveso incident; it is hoped that many of the questions concerning the mutagenicity of TCDD and possibly of other dioxin congeners will be answered as a result of this work.

Acridines↗

An assessment of the potential testicular toxicity of 10 pesticides using the mouse-sperm morphology assay.

Dinitrobutylphenol, chlorbenzilate, atrazine, Ordram, Telone (dichloropropene), pentachlorophenol (technical and reagent grades), Benomyl, DBCP (dibromochloropropane), and carbaryl were tested over a range of 7 doses in the mouse to assess their testicular toxicity. Measures of potential toxicity were sperm morphology, sperm counts and testicular weights. Each pesticide was injected intra-peritoneally in a single dose on each of 5 days. Testicular toxicity was assessed at 35 days. None of the pesticides tested, including the known human male testicular toxin, DBCP, produced statistically significant differences in the parameters from vehicle-injected controls.

Animals↗

Inability of chlorophenols to induce 6-thioguanine-resistant mutants in V79 Chinese hamster cells.

The induction of mutation at the hypoxanthine-guanine phosphoribosyl transferase locus and cytotoxicities of 6 different chlorophenols (2,4- and 2,6-dichlorophenol, 2,4,5- and 2,4,6-trichlorophenol, 2,3,4,6-tetrachlorophenol and pentachlorophenol) were examined in V79 Chinese hamster cells without exogenous metabolic activation. The chlorophenols were cytotoxic to V79 cells, but failed to produce significant increases in the frequency of 6-thioguanine-resistant mutants.

Animals↗

In vitro DNA binding of 2-amino-3-methylimidazo(4,5-f)[5-3H]quinoline (IQ) is modulated by sulfotransferase and sulfate levels.

DNA binding in vitro was measured with 2-amino-3- methylimidazo(4,5-f)[5-3H]quinoline (3H-IQ) in the presence of S9 and microsomes from Wistar rat liver. DNA binding of 3H-IQ was catalyzed by both microsomes and S9 and was increased 5-fold in Aroclor (PCB)-pretreated animals. DNA binding was reduced by the specific inhibitor of sulfotransferase 2,6-dichloro-4-nitrophenol and slightly increased by 3'-phosphoadenosine 5'-phosphosulfate. The incubation of IQ in media with increasing concentrations of sulfate produced a modest dose-dependent increase in DNA binding. Liver S9 obtained from rats which had been administered 1% sulfite in drinking water catalyzed a higher binding of IQ to DNA, and this effect was inhibited by pentachlorophenol. The data demonstrate that sulfotransferase has a role in the activation of IQ and that variations in the activity of this enzyme induced by dietary changes may vary the genotoxic activity of IQ.

Animals↗

Inhibition of sulfotransferase affecting unscheduled DNA synthesis induced by 2-acetylaminofluorene: an in vivo and in vitro comparison.

The unscheduled DNA repair (UDS) assay was conducted using the in vivo and in vitro procedures to investigate the role of arylsulfotransferases (AST) in the genotoxicity of 2-acetylaminofluorene (AAF). The in vivo assay had 4 groups of rats that consisted of those treated with pentachlorophenol (PCP), PCP and AAF, or AAF and an untreated control. The in vitro assay used hepatocytes from 3-methylcholanthrene or corn oil (control) treated rats. In both the in vivo and in vitro UDS assays AAF induced DNA damage. PCP, an inhibitor of arylsulfotransferase, significantly decreased AAF induced DNA damage. In the in vivo assay, PCP induced a significant increase in UDS and confounded an investigation of the role of sulfotransferase. The in vitro UDS assay more clearly defined the effect of PCP on AAF genotoxicity.

2-Acetylaminofluorene↗

Effect of inhibitors of electron transport and oxidative phosphorylation on Trypanosoma cruzi respiration and growth.

Antimycin A and 2-heptyl-4-hydroxyquinoline N-oxide, two specific inhibitors of the b-c1 segment of the respiratory chain, affected the respiration of Trypanosoma cruzi epimastigote forms. The half-maximum inhibitory concentrations were about 0.05 and 4.0 micrograms/mg cells (dry wt.), respectively. The maximum effect of antimycin (about 80% inhibition of respiration) was at about 0.1 microgram antimycin/mg cells. Differential spectrophotometry of T. cruzi epimastigotes in the presence of antimycin, cyanide (or sulfide) and uncouplers, revealed the presence of functional cytochromes aa3, b and c558. In the stationary growth phase respiration by T. cruzi was completely inhibited by cyanide and effectively inhibited by sulfide, but in the exponential growth phase respiration was about 20% insensitive to 5 mM cyanide. Cyanide- and antimycin-insensitive respiration was completely inhibited by salicylhydroxamic acid (2 mM). Antimycin inhibited the operation of the tricarboxylic acids cycle in T. cruzi, as shown by the lesser production of 14CO2 and by the modification of 14C distribution in epimastigotes incubated with [1-14C]glucose, [2-14C]acetate or NaH14CO3. The inhibition of electron transport by antimycin increased the rate of the fumarate reductase reaction, an alternative electron pathway for the oxidation of reduced pyridine nucleotides. Addition of carbonyl cyanide 3-chlorophenylhydrazone to epimastigotes increased the rate of respiration and promoted the oxidation of reduced cytochrome b components, thus showing that these components are subject to respiratory (acceptor) control. Pentachlorophenol similarly affected the cytochrome b redox level but did not modify the rate of respiration. The uncouplers released N,N'-dicyclohexylcarbodiimide inhibition of respiration, and uncouplers and cyanide significantly decreased the ATP level in epimastigotes. The combined effects of the assay inhibitors on respiration, cytochrome b redox level, ATP content and energy charge confirmed the operation of oxidative phosphorylation in T. cruzi epimastigotes. Antimycin, uncouplers and N,N'-dicyclohexylcarbodiimide inhibited growth of T. cruzi, thus proving the essential role of oxidative phosphorylation for the parasite.

Adenosine Triphosphate↗

Distribution, metabolism and excretion of pentachloroanisole in the beagle dog and miniature pig.

Tissue distribution, excretion and metabolism studies of pentachloroanisole (PCA), an environmental metabolite of pentachlorophenol (PCP), were conducted in the beagle dog and miniature pig following single oral doses (25 mg/kg) of radiolabelled PCA. PCA was readily demethylated by both species, with a half-life of 5-8 min. The resultant PCP was the major metabolite in dogs and pigs. In the dog, an average of 21.9% of the administered radiolabel was excreted in the urine and 62.3% in the faeces during a 7-day period. Of the tissues analysed, an average of 3.2% of the radiolabel remained in the liver, and blood and muscle accounted for averages of 3.0 and 2.3%, respectively, of the dose. Free and conjugated PCP were found in the urine of dogs; no PCA or tetrachlorohydroquinone (TCH) were found. In dog faeces, PCP and a trace of polar material were observed; no PCA was excreted in dog faeces. In the miniature pig, an average of 25.8% of the administered radiolabel was excreted in the urine and 32.0% in the faeces during a 2-wk period. An average of 4.4% of the radiolabel was found in the liver, 8.8% in the blood, 7.1% in the muscle and 6.4% in the fat. In pig urine, PCP and conjugated PCP were the only metabolites observed; no PCA or TCH was found. Pig faeces contained a trace of unchanged PCA; PCP and polar metabolites were also found. Since pig tissues retained a sizeable residue 2 wk after a single dose of PCA, various agents were used in an attempt to decrease the tissue level of radiolabel in pigs; anion exchange resin was found to be the most effective.

Animals↗