In vivo genotoxicity of sodium ortho-phenylphenol: phenylbenzoquinone is one of the DNA-binding metabolite(s) of sodium ortho-phenylphenol

Human Health Effects of Biphenyl: Key Findings and Scientific Issues

BACKGROUND

In support of the Integrated Risk Information System (IRIS), the U.S. Environmental Protection Agency (EPA) has evaluated the human health hazards of biphenyl exposure.

OBJECTIVES

We review key findings and scientific issues regarding expected human health effects of biphenyl.

METHODS

Scientific literature from 1926 through September 2012 was critically evaluated to identify potential human health hazards associated with biphenyl exposure. Key issues related to the carcinogenicity and noncancer health hazards of biphenyl were examined based on evidence from experimental animal bioassays and mechanistic studies.

DISCUSSION

Systematic consideration of experimental animal studies of oral biphenyl exposure took into account the variety of study designs (e.g., study sizes, exposure levels, and exposure durations) to reconcile differing reported results. The available mechanistic and toxicokinetic evidence supports the hypothesis that male rat urinary bladder tumors arise through urinary bladder calculi formation but is insufficient to hypothesize a mode of action for liver tumors in female mice. Biphenyl and its metabolites may induce genetic damage, but a role for genotoxicity in biphenyl-induced carcinogenicity has not been established.

CONCLUSIONS

The available health effects data for biphenyl provides suggestive evidence for carcinogenicity in humans, based on increased incidences of male rat urinary bladder tumors at high exposure levels and on female mouse liver tumors. Kidney toxicity is also a potential human health hazard of biphenyl exposure.

CITATION

Li Z, Hogan KA, Cai C, Rieth S. 2016. Human health effects of biphenyl: key findings and scientific issues. Environ Health Perspect 124:703-712; http://dx.doi.org/10.1289/ehp.1509730.

The role of urinary pH in o-phenylphenol-induced cytotoxicity and chromosomal damage in the bladders of F344 rats

o-Phenylphenol (OPP) is a widely used fungicide and antibacterial agent that at high doses has been shown to cause bladder cancer in male F344 rats. The mechanisms underlying OPP-induced bladder carcinogenicity remain unclear but it has been proposed that a non-enzymatic pH-dependent autoxidation of phenylhydroquinone (PHQ), a primary metabolite of OPP, may be a key step in OPP-induced rat bladder carcinogenesis. To investigate this mechanism and to provide insights into the potential human health relevance of OPP-induced cancer, a series of in vitro and in vivo experiments were conducted. In human lymphoblastoid TK-6 cells and rat bladder epithelial NBT-II cells, strong increases in cytotoxicity were seen at a constant concentration of PHQ by increasing the buffer pH as well as by increasing concentrations of PHQ at a constant pH. In in vivo studies, male rats were administered OPP (4,000 and 8,000 ppm) in a diet supplemented with either 1% ammonium chloride or 3% sodium bicarbonate to produce acidic and alkaline urinary pH, respectively. Significant increases in cell proliferation as detected by 5-bromo-2'-deoxyuridine incorporation and micronucleus formation were seen in the bladder cells of OPP-treated rats with neutral or alkaline urinary pH but not in animals with the acidified urine. The results from these in vitro and in vivo studies provide support for the autoxidation hypothesis of bioactivation, and provide additional evidence that urinary pH can significantly influence the genotoxicity and carcinogenicity of this important agent.

Analysis of genotoxicity and the carcinogenic mode of action for ortho-phenylphenol

Ortho-phenylphenol (OPP) and its sodium salt (SOPP) are commercial products that have wide human exposure and have been shown in several studies to be rodent carcinogens. Genetic toxicology data were assessed in an attempt to understand the carcinogenic mode of action of OPP and SOPP. More than 130 studies were evaluated to determine if OPP, SOPP, or any of their enzymatic or nonenzymatic breakdown products react directly with DNA to induce mutation, changes in chromosome structure or number, DNA repair, or nonspecific DNA damage including strand breakage or covalent binding. The genotoxicity databases for OPP and SOPP are not only large but heterogeneous, requiring weight-of-evidence methods to arrive at a conclusion regarding their genotoxic properties and potential. Evidence derived from the available studies leads to the conclusion that study results showing OPP/SOPP directly interacting with DNA are equivocal. Clastogenicity was the most consistent type of genetic toxicity produced by OPP/SOPP (and their break-down products) and was consistently associated with other intracellular preneoplastic toxicity produced at super-threshold concentrations. The weight of evidence from the combined database supports the hypothesis that OPP/SOPP-induced DNA damage is a threshold-dependent response associated with target tissue toxicity, most likely induced by their breakdown products phenylhydroquinone and phenylbenzoquinone. It is possible that this threshold-dependent clastogenicity could contribute to the carcinogenic mode of action for OPP or SOPP.

Monitoring of DNA Adducts in Humans and 32P-Postlabelling Methods. A Review

DNA adduct formation in humans is a promising biomarker for elucidating the molecular epidemiology of cancer. For detection of DNA adducts, the most widely used methods include mass spectroscopy, fluorescence spectroscopy, immunoassays and 32P-postlabelling. Among them, the 32P-postlabelling method appears to meet best the criteria of sensitivity and amount of DNA needed, and, therefore, is one of the most appropriate methods for biomonitoring of human DNA adducts. Most classes of carcinogens have been subjected to 32P-postlabelling analysis, ranging from bulky and/or aromatic compounds to small and/or aliphatic compounds; it has also been used, with modifications, to detect apurinic sites in DNA, oxidative damage to DNA, UV-induced photodimers and, to a lesser extent, DNA damage caused by cytotoxic drugs. It has been used in human biomonitoring studies to detect DNA damage from occupational exposure to carcinogens, and also from environmental (i.e. non-occupational) exposures. It has also led to the discovery of the presence of numerous modifications in DNA arising from endogenous processes. The principle of the method is the enzymatic digestion of DNA to nucleotides, 5'-labelling of these nucleotides with an isotopically labelled phosphate group, and the resolution, detection and quantitation of the labelled products. Since the development of the original procedure in the early 1980s, many methods have been developed to increase the sensitivity by enrichment of modified nucleotides prior to labelling. The review presents the individual 32P-postlabelling techniques (standard procedure, enrichment methods) and a critical evaluation of these assays, besides reviewing the applications of the method to different DNA modifications, and its utilization in human biomonitoring studies. A review with 179 references.

O-phenylphenol and its sodium and potassium salts: a toxicological assessment

Ortho-phenylphenol (OPP) and its sodium (SOPP) and potassium (POPP) salts are used as fungicides and disinfectants. Due to the widespread use of especially OPP and SOPP, the potential for consumer exposure and some "critical" findings the toxicological database is quite extensive and complex. In experimental animals toxicity after single oral and dermal administration of these compounds is low. For the skin and mucous membranes, OPP has to be considered as irritating, and SOPP and POPP as corrosive. A large number of chronic toxicity and reproduction studies did not show any indication of oestrogen-like or other endocrine effects of OPP in the mammalian organism. No teratogenic effects were observed after the administration of OPP or SOPP in rats, mice, and rabbits. In two-generation studies in rats, OPP did not affect reproduction. The available data do not suggest a relevant potential for immunotoxic properties. The administration of high dietary concentrations of OPP to mice up to 2 years induced hepatocellular changes indicative of adaptations to metabolic demands, zonal degeneration, focal hepatocellular necrosis, and/or pigmentation of the liver. Only in male mice of one study, using a strain prone to develop hepatocellular tumors at high spontaneous incidences, the incidence of hepatocellular adenomas was increased. The incidence of hepatocellular carcinomas was not affected by treatment. The urothel of the urinary bladder (at very high doses also of the renal pelvis and the papilla) is the main target tissue after the repeated oral exposure of rats. The changes initially consist of increased mitosis, followed by simple epithelial hyperplasia, developing to a papillary and/or nodular form, later on to papillomas and transitional carcinomas. Crystals or stones in the bladder do not play a decisive role in this cascade. SOPP is more effective than OPP in this respect. Male rats are much more sensitive than females. In mice, hamsters, guinea pigs, and dogs, urothelial lesions do not develop even at very high oral dose levels. The findings in rats explain why there is a large genotoxicity/mutagenicity data base not only for OPP and SOPP but also for their metabolites on nearly all kinds of endpoints/targets. The weight of evidence suggests that genotoxicity of OPP/SOPP or their metabolites does not play a decisive role for the carcinogenicity at the urothel. Among them are lack of DNA binding of OPP to the rat bladder epithelium, the differences between OPP and SOPP, between male and female rats, between rats and mice (despite roughly comparable toxicokinetics), as well as the fact that tumors develop only at dose levels inducing hyperplasias. In addition, the strong dependence of the incidence and severity of the nonneoplastic and neoplastic bladder changes on urinary pH values (modified by feeding of ammonium chloride or sodium hydrogen carbonate) is consistent with the hypothesis of a nongenotoxic mode of action. Finally, there is no correlation between the urinary concentration of OPP or its metabolites and the incidence of hyperplasias/tumors in the urinary bladder. Both tumorigenic effects in rats and male mice are considered to represent high-dose, sex- and/or species-specific phenomena, based on nongenotoxic mechanisms of action and therefore allow the conclusion that the conventional margin of safety approaches are appropriate when assessing the risk of applications of OPP and its salts.

The comet assay with multiple mouse organs: comparison of comet assay results and carcinogenicity with 208 chemicals selected from the IARC monographs and U.S. NTP Carcinogenicity Database

The comet assay is a microgel electrophoresis technique for detecting DNA damage at the level of the single cell. When this technique is applied to detect genotoxicity in experimental animals, the most important advantage is that DNA lesions can be measured in any organ, regardless of the extent of mitotic activity. The purpose of this article is to summarize the in vivo genotoxicity in eight organs of the mouse of 208 chemicals selected from International Agency for Research on Cancer (IARC) Groups 1, 2A, 2B, 3, and 4, and from the U.S. National Toxicology Program (NTP) Carcinogenicity Database, and to discuss the utility of the comet assay in genetic toxicology. Alkylating agents, amides, aromatic amines, azo compounds, cyclic nitro compounds, hydrazines, halides having reactive halogens, and polycyclic aromatic hydrocarbons were chemicals showing high positive effects in this assay. The responses detected reflected the ability of this assay to detect the fragmentation of DNA molecules produced by DNA single strand breaks induced chemically and those derived from alkali-labile sites developed from alkylated bases and bulky base adducts. The mouse or rat organs exhibiting increased levels of DNA damage were not necessarily the target organs for carcinogenicity. It was rare, in contrast, for the target organs not to show DNA damage. Therefore, organ-specific genotoxicity was necessary but not sufficient for the prediction of organ-specific carcinogenicity. It would be expected that DNA crosslinkers would be difficult to detect by this assay, because of the resulting inhibition of DNA unwinding. The proportion of 10 DNA crosslinkers that was positive, however, was high in the gastrointestinal mucosa, stomach, and colon, but less than 50% in the liver and lung. It was interesting that the genotoxicity of DNA crosslinkers could be detected in the gastrointestinal organs even though the agents were administered intraperitoneally. Chemical carcinogens can be classified as genotoxic (Ames test-positive) and putative nongenotoxic (Ames test-negative) carcinogens. The Ames test is generally used as a first screening method to assess chemical genotoxicity and has provided extensive information on DNA reactivity. Out of 208 chemicals studied, 117 are Ames test-positive rodent carcinogens, 43 are Ames test-negative rodent carcinogens, and 30 are rodent noncarcinogens (which include both Ames test-positive and negative noncarcinogens). High positive response ratio (110/117) for rodent genotoxic carcinogens and a high negative response ratio (6/30) for rodent noncarcinogens were shown in the comet assay. For Ames test-negative rodent carcinogens, less than 50% were positive in the comet assay, suggesting that the assay, which detects DNA lesions, is not suitable for identifying nongenotoxic carcinogens. In the safety evaluation of chemicals, it is important to demonstrate that Ames test-positive agents are not genotoxic in vivo. This assay had a high positive response ratio for rodent genotoxic carcinogens and a high negative response ratio for rodent genotoxic noncarcinogens, suggesting that the comet assay can be used to evaluate the in vivo genotoxicity of in vitro genotoxic chemicals. For chemicals whose in vivo genotoxicity has been tested in multiple organs by the comet assay, published data are summarized with unpublished data and compared with relevant genotoxicity and carcinogenicity data. Because it is clear that no single test is capable of detecting all relevant genotoxic agents, the usual approach should be to carry out a battery of in vitro and in vivo tests for genotoxicity. The conventional micronucleus test in the hematopoietic system is a simple method to assess in vivo clastogenicity of chemicals. Its performance is related to whether a chemical reaches the hematopoietic system. Among 208 chemicals studied (including 165 rodent carcinogens), 54 rodents carcinogens do not induce micronuclei in mouse hematopoietic system despite the positive finding with one or two in vitro tests. Forty-nine of 54 rodent carcinogens that do not induce micronuclei were positive in the comet assay, suggesting that the comet assay can be used as a further in vivo test apart from the cytogenetic assays in hematopoietic cells. In this review, we provide one recommendation for the in vivo comet assay protocol based on our own data.

Oxidative damage to cellular and isolated DNA by metabolites of a fungicide ortho-phenylphenol

ortho-Phenylphenol (OPP) and its sodium salt, which are used as fungicides and antibacterial agents, have been found to cause carcinomas in the urinary tract of rats. To clarify the carcinogenic mechanism of OPP, we compared the DNA damage inducing ability of an OPP metabolite, phenyl-1,4-benzoquinone (PBQ) with that of another metabolite, phenylhydroquinone (PHQ). Pulsed field gel electrophoresis showed that PBQ and PHQ induced DNA strand breakage in cultured human cells, but PBQ did it more efficiently than PHQ. Significant increases in 8-oxo-7,8-dihydro-2'-deoxyguanosine (8-oxodG) were observed in cells treated with PBQ and PHQ, and the increase of 8-oxodG induced by PBQ was significantly higher than that induced by PHQ. Using 32P-5'-end-labeled DNA fragments obtained from human p53 tumor suppressor gene and c-Ha-ras-1 protooncogene, we showed that PBQ plus NADH, and also PHQ, induced DNA damage frequently at thymine residues, in the presence of Cu(II). The intensity of DNA damage by PBQ was stronger than that by PHQ, showing higher importance of PBQ than other OPP metabolites. Catalase and bathocuproine inhibited Cu(II)-mediated DNA damage by PBQ plus NADH and PHQ, suggesting that H2O2 reacts with Cu(I) to produce active species causing DNA damage. Electron spin resonance and UV-visible spectroscopic studies have demonstrated generation of semiquinone radical and superoxide from the reaction of PBQ with NADH or the Cu(II)-mediated autoxidation of PHQ. The present results suggest that these OPP metabolites cause oxidative DNA damage through H2O2 generation in cells, and the damage may lead to mutation and carcinogenesis. It is concluded that PBQ may play a more important role in the expression of OPP carcinogenicity than other OPP metabolites.

Urinary physiologic and chemical metabolic effects on the urothelial cytotoxicity and potential DNA adducts of o-phenylphenol in male rats

ortho-Phenylphenol (OPP), a fungicide and antibacterial agent with food residues, is carcinogenic to rat bladder. The present studies provide information on changes in urinary composition and urinary metabolites, urothelial cytotoxicity and regenerative hyperplasia, and DNA adducts in male F344 rats fed OPP. An initial experiment evaluated dietary doses of 0, 1,000, 4,000, and 12,500 ppm OPP fed for 13 weeks. There was no evidence of urinary calculi, microcrystalluria, or calcium phosphate-containing precipitate, but urothelial cytotoxicity and hyperplasia occurred at the highest dose only. In a second experiment, rats were fed dietary OPP levels of 0, 800, 4,000, 8,000, and 12,500 ppm. Urinary pH was > 7 in all groups. Urinary volume was increased at the 2 highest doses with consequent decreases in osmolality, creatinine, and other solutes. Total urinary OPP metabolite excretions were increased, mostly excreted as conjugates of OPP and of phenylhydroquinone. Free OPP or free metabolites accounted for less than 2% excreted in the urine without a dose response. Urothelial toxicity and hyperplasia occurred only at doses of 8,000 and 12,500 ppm. OPP-DNA adducts were not detected in the urothelium at any dose. In summary, OPP produces cytotoxicity and proliferation of the urothelium at dietary doses > or = 8,000 ppm without formation of urinary solids. The paucity of unconjugated metabolites and the lack of OPP-DNA adducts suggests that OPP is acting as a bladder carcinogen in male rats by inducing cytotoxicity and hyperplasia without it or its metabolites directly binding to DNA.

In vivo genotoxicity of ortho-phenylphenol, biphenyl, and thiabendazole detected in multiple mouse organs by the alkaline single cell gel electrophoresis assay

In Japan, ortho-phenylphenol (OPP), biphenyl (BP), and thiabendazole (2-(4'-thiazolyl)benzimidazole, TBZ) are commonly used as a postharvest treatment to preserve imported citrus fruits during transport and storage. We used a modification of the alkaline single cell gel electrophoresis (SCG) (Comet) assay to test the in vivo genotoxicity of those agents in mouse stomach, liver, kidney, bladder, lung, brain, and bone marrow. CD-1 male mice were sacrificed 3, 8, and 24 h after oral administration of the test compounds. OPP (2000 mg/kg) induced DNA damage in the stomach, liver, kidney, bladder, and lung, BP (2000 mg/kg) and TBZ (200 mg/kg) induced DNA damage in all the organs studied. For OPP, increased DNA damage peaked at 3-8 h and tended to decrease at 24 h. For BP, on the contrary, increased DNA migration peaked at 24 h. That delay may have been due to the fact that OPP is metabolized by cytochrome 450 and prostaglandin H synthase to phenylbenzoquinone (PBQ), a DNA binding metabolite, and BP is metabolized to PBQ via OPP and m-phenylphenol. The positive response to TBZ, an aneugen, supports the in vivo DNA-damaging action of TBZ.

Postlabeling: a sensitive method for studying DNA adducts and their role in carcinogenesis

The covalent binding of xenobiotics to DNA is an important trigger of the multistage process that leads to carcinogenesis. 32P-postlabeling represents a highly sensitive method for biomonitoring exposure to genotoxic agents and for cancer risk assessment; it is capable of detecting less than one DNA adduct per human genome. Recent improvements to the technique have shown that the resistance of adducted DNA to enzyme digestion may lead to an overestimation of the number of different adducts present in a sample.

Genotoxic effects of the o-phenylphenol metabolites phenylhydroquinone and phenylbenzoquinone in V79 cells

o-Phenylphenol (OPP) and its sodium salt, sodium o-phenylphenate are broad spectrum fungicides and disinfectants with widespread usage. Both chemicals have been reported to induce cancer in the kidney and urinary bladder of Fischer 344 rats. Recently it has been proposed that the metabolic activation of OPP occurs via a two-step process involving the cytochrome P450-mediated formation of phenylhydroquinone (PHQ) in the liver and a prostaglandin H synthase-mediated oxidation of PHQ to phenylbenzoquinone (PBQ) in the urinary tract. In order to further investigate the metabolic activation and genotoxic effects of OPP, we have investigated the ability of PHQ and PBQ to induce micronuclei and mutations at the HGPRT locus in a prostaglandin H synthase-containing V79 Chinese hamster lung fibroblast cell line. In arachidonic acid-supplemented V79 cells, PHQ induced a significant increase in micronuclei whereas no increase was observed in cells in the absence of arachidonic acid supplementation. Immunofluorescent labeling of centromeric proteins with the CREST antibody indicated that the arachidonic acid-dependent induction of micronuclei by PHQ was due almost entirely to micronuclei containing whole chromosomes which had failed to segregate properly during mitosis. The induction of micronuclei by PHQ was significantly inhibited by treatment of the cells with indomethacin, aspirin, ascorbic acid, dithiothreitol and reduced glutathione supporting a role for prostaglandin H synthase in the genotoxic effects of PHQ. No increase in 6-thioguanine-resistant cells was observed in cells treated with PHQ or PBQ. This arachidonic acid-dependent conversion of PHQ to a genotoxic species is consistent with the hypothesis that a prostaglandin H synthase-mediated activation of PHQ may be involved in OPP- and SOPP-induced urinary tract carcinogenesis and also suggests that the induction of aneuploidy may play an important role in OPP-induced tumorigenesis.