Helicobacter pylori does not mediate the formation of carcinogenic N-nitrosamines.

BACKGROUND: Both N-nitroso compounds and colonization with Helicobacter pylori represent known risk-factors for the development of gastric cancer. Endogenous formation of N-nitroso compounds is thought to occur predominantly in acidic environments such as the stomach. At neutral pH, bacteria can catalyze the formation of N-nitroso compounds. Based on experiments with a noncarcinogenic N-nitroso compound as end product, and using only a single H. pylori strain, it was recently reported that H. pylori only displays a low nitrosation capacity. As H. pylori is a highly diverse bacterial species, it is reasonable to question the generality of this finding. In this study, several genetically distinct H. pylori strains are tested for their capacity to form carcinogenic N-nitrosamines. MATERIALS AND METHODS: Bacteria were grown in the presence of 0-1000 microM morpholine and nitrite (in a 1 : 1 molar ratio), at pH 7, 5 and 3. RESULTS: Incubation of Neisseria cinerea (positive control) with 500 microM morpholine and 500 microM nitrite, resulted in a significant increase in formation of N-nitrosomorpholine, but there was no significant induction of N-nitrosomorpholine formation by any of the H. pylori strains, at any of the three pH conditions. CONCLUSION: H. pylori does not induce formation of the carcinogenic N-nitrosomorpholine in vitro. The previously reported weak nitrosation capacity of H. pylori is not sufficient to nitrosate the more difficulty nitrosatable morpholine. This probably also holds true for other secondary amines. These results imply that the increased incidence of gastric cancer formation that is associated with gastric colonization by H. pylori is unlikely to result from the direct induced formation of carcinogenic nitrosamines by H. pylori. However, this has to be further confirmed in in vivo studies.

Pesticides and nitrate in groundwater and rainwater in the Province of Limburg in The Netherlands.

The purpose of this study was to investigate the occurrence of high levels of pesticides in groundwater and rainwater in The Province of Limburg in The Netherlands. In groundwater samples in particular the presence of triazines--atrazine, simazine and propazine--was observed; besides these pesticides, dieldrin has also been observed. Atrazine and simazine were found to exceed the groundwater standard of 100 ng L(-1). In the rainwater samples, the presence of 13 of 23 different analyzed pesticides was observed. A number of pesticides were found in high concentrations; e.g. atrazine (>200 ng L(-1)). Two pesticides detected in rainwater (beta+gamma-HCH and atrazine) were found to exceed the groundwater standard. Seven pesticides in rainwater were found to exceed the target value and three pesticides the maximum tolerable risk value (DDT, heptachlor and heptachlorepoxide A), which are used as ecotoxicological standards in The Netherlands. Nitrate in 15 of 16 analyzed natural springs was found to exceed the guideline value for nitrate in drinking water of 50 mg L(-1), up to levels of about 200 mg L(-1). Nitrate concentrations in rainwater samples were observed up to 4.5 mg L(-1). A risk analysis of exposure to high pesticide levels in groundwater or rainwater has been performed using the model HESP. For atrazine levels due to deposition of rainwater in two different locations, exceedance of the T.D.I. level of 0.5 microg kg(-1) day(-1) based on WHO criteria was observed for children using both an urban and a rural scenario and use of groundwater as drinking water.

Intragastric volatile N-nitrosamines, nitrite, pH, and Helicobacter pylori during long-term treatment with omeprazole.

BACKGROUND & AIMS: This study evaluated the effect of long-term gastric acid suppressive therapy with omeprazole on intragastric levels of carcinogenic N-nitrosamines and related parameters. METHODS: Forty-five patients on long-term omeprazole medication (mean, 35 months) and 13 healthy subjects without medication participated. Volatile N-nitrosamines were determined in gastric juice and urine. Intragastric pH, nitrite, nitrate, and H. pylori status were determined. DNA isolated from gastric biopsy specimens was analyzed for precarcinogenic alkyl-DNA adducts. RESULTS: The intragastric pH in patients was significantly higher compared with controls (P = 0.0001). Gastric nitrite levels in patients were nonsignificantly higher. There was no difference in total levels of intragastric volatile N-nitrosamines between patients and controls, however, urinary N-nitrosodimethylamine excretion was higher in patients (P = 0.001). On omeprazole, Helicobacter pylori-positive vs. -negative patients had a nonsignificantly higher intragastric nitrite level and higher urinary N-nitrosodimethylamine excretion. No alkyl-DNA adducts could be detected in gastric epithelium. CONCLUSIONS: Increased intragastric pH caused by long-term treatment with omeprazole does not result in increased intragastric levels of nitrite and volatile N-nitrosamines. The significantly higher urinary N-nitrosamine excretion implies the risk of increased endogenous formation of N-nitrosamines during long-term omeprazole treatment. This risk may be higher in H. pylori-positive patients.

Excretion of volatile nitrosamines in a rural population in relation to food and drinking water consumption.

Urinary excretion of volatile nitrosamines was assessed in 59 non-smokers living in a rural county of Québec, Canada. Water and food intakes were measured by means of a 24-hour recall. Nitrates were analyzed in the tap water of all participants (geometric mean=2.0 mg nitrate-N/L) and dietary intakes of nitrate and vitamins C and E were estimated via a validated Canadian food database. Urine was collected over the same 24-hour period and analyzed for nitrates by hydrazine reduction and for volatile nitrosamines by gas-chromatography/mass spectrometry. N-Nitrosopiperidine (NPIP) was found in urine samples from 52 of the 59 subjects. Geometric mean of NPIP urinary excretion was 67 ng/day and maximum value was 1045 ng/day. No other volatile nitrosamine was detected. There was a correlation between urinary nitrate excretion and total nitrate intake (r=0.71, P < 0.001). However, no relationship was found between urinary NPIP excretion and either nitrate excretion, dietary or water nitrate intakes. NPIP excretion was significantly correlated to coffee intake (r=0.40, P=0.002) and this relation was not modified by vitamin intake. We conclude that nitrate intake is not related to nitrosamine excretion in this rural population. The influence of coffee consumption on NPIP excretion deserves further attention.

Evaluation of fecal mutagenicity and colorectal cancer risk.

Colorectal cancer is one of the most common internal malignancies in Western society. The cause of this disease appears to be multifactorial and involves genetic as well as environmental aspects. The human colon is continuously exposed to a complex mixture of compounds, which is either of direct dietary origin or the result of digestive, microbial and excretory processes. In order to establish the mutagenic burden of the colorectal mucosa, analysis of specific compounds in feces is usually preferred. Alternatively, the mutagenic potency of fecal extracts has been determined, but the interpretation of these more integrative measurements is hampered by methodological shortcomings. In this review, we focus on exposure of the large bowel to five different classes of fecal mutagens that have previously been related to colorectal cancer risk. These include heterocyclic aromatic amines (HCA) and polycyclic aromatic hydrocarbons (PAH), two exogenous factors that are predominantly ingested as pyrolysis products present in food and (partially) excreted in the feces. Additionally, we discuss N-nitroso-compounds, fecapentaenes and bile acids, all fecal constituents (mainly) of endogenous origin. The mutagenic and carcinogenic potency of the above mentioned compounds as well as their presence in feces, proposed mode of action and potential role in the initiation and promotion of human colorectal cancer are discussed. The combined results from in vitro and in vivo research unequivocally demonstrate that these classes of compounds comprise potent mutagens that induce many different forms of genetic damage and that particularly bile acids and fecapentaenes may also affect the carcinogenic process by epigenetic mechanisms. Large inter-individual differences in levels of exposures have been reported, including those in a range where considerable genetic damage can be expected based on evidence from animal studies. Particularly, however, exposure profiles of PAH and N-nitroso compounds (NOC) have to be more accurately established to come to a risk evaluation. Moreover, lack of human studies and inconsistency between epidemiological data make it impossible to describe colorectal cancer risk as a result of specific exposures in quantitative terms, or even to indicate the relative importance of the mutagens discussed. Particularly, the polymorphisms of genes involved in the metabolism of heterocyclic amines are important determinants of carcinogenic risk. However, the present knowledge of gene-environment interactions with regard to colorectal cancer risk is rather limited. We expect that the introduction of DNA chip technology in colorectal cancer epidemiology will offer new opportunities to identify combinations of exposures and genetic polymorphisms that relate to increased cancer risk. This knowledge will enable us to improve epidemiological study design and statistical power in future research.

Does the risk of childhood diabetes mellitus require revision of the guideline values for nitrate in drinking water?

In recent years, several studies have addressed a possible relationship between nitrate exposure and childhood type 1 insulin-dependent diabetes mellitus. The present ecologic study describes a possible relation between the incidence of type 1 diabetes and nitrate levels in drinking water in The Netherlands, and evaluates whether the World Health Organization and the European Commission standard for nitrate in drinking water (50 mg/L) is adequate to prevent risk of this disease. During 1993-1995 in The Netherlands, 1,104 cases of type 1 diabetes were diagnosed in children 0-14 years of age. We were able to use 1,064 of these cases in a total of 2,829,020 children in this analysis. We classified mean nitrate levels in drinking water in 3,932 postal code areas in The Netherlands in 1991-1995 into two exposure categories. One category was based on equal numbers of children exposed to different nitrate levels (0.25-2.08, 2.10-6.42, and 6.44-41.19 mg/L nitrate); the other was based on cut-off values of 10 and 25 mg/L nitrate. We determined standardized incidence ratios (SIRs) for type 1 diabetes in subgroups of the 2,829,020 children with respect to both nitrate exposure categories, sex, and age and as compared in univariate analysis using the chi-square test for trend. We compared the incidence rate ratios (IRRs) by multivariate analysis in a Poisson regression model. We found an effect of increasing age of the children on incidence of type 1 diabetes, but we did not find an effect of sex or of nitrate concentration in drinking water using the two exposure categories. For nitrate levels > 25 mg/L, an increased SIR and an increased IRR of 1.46 were observed; however, this increase was not statistically significant, probably because of the small number of cases (15 of 1,064). We concluded that there is no convincing evidence that nitrate in drinking water at current exposure levels is a risk factor for childhood type 1 diabetes mellitus in The Netherlands, although a threshold value > 25 mg/L for the occurrence of this disease can not be excluded.

In vitro effects of coal fly ashes: hydroxyl radical generation, iron release, and DNA damage and toxicity in rat lung epithelial cells.

Oxygen radical generation due to surface radicals, inflammation, and iron release has been suggested as the mechanism of adverse effects of quartz, such as emphysema, fibrosis, and carcinogenic effects. Therefore, we measured iron release, acellular generation of hydroxyl radicals, and oxidative DNA damage and cytotoxicity in rat lung epithelial (RLE) cells by different coal fly ashes (CFA) that contain both quartz and iron. Seven samples of CFA with different particle size and quartz content (up to 14.1%) were tested along with silica (alpha-quartz), ground coal, and coal mine dust (respirable) as positive control particles, and fine TiO(2) (anatase) as a negative control. Five test samples were pulverized fuel ashes (PFA), two samples were coal gasification (SCG) ashes (quartz content <0.1%), and one sample was a ground coal. No marked differences between SCG and PFA fly ashes were observed, and toxicity did not correlate with physicochemical characteristics or effect parameters. Stable surface radicals were only detected in the reference particles silica and coal mine dust, but not in CFA. On the other hand, hydroxyl radical generation by all fly ashes was observed in the presence of hydrogen peroxide, which was positively correlated with iron mobilization and inhibited by deferoxamine, but not correlated with iron or quartz content. Also a relationship between acellular hydroxyl radical generation and oxidative DNA damage in RLE cells by CFA was observed. Differences in hydroxyl radical generation and oxidative damage by the CFA were not related to iron and quartz content, but the respirable ashes (MAT023, 38, and 41) showed a very extensive level of hydroxyl radical generation in comparison to nonrespirable fly ashes and respirable references. This radical generation was clearly related to the iron mobilization from these particles. In conclusion, the mechanisms by which CFA and the positive references (silica, coal mine dust) affect rat lung epithelial cells seem to be different, and the data suggest that quartz in CFA does not act the same as quartz in silica or coal mine dust. On the other hand, the results indicate an important role for size and iron release in generation and subsequent effects of reactive oxygen species caused by CFA.

Effect of ascorbic acid and green tea on endogenous formation of N-nitrosodimethylamine and N-nitrosopiperidine in humans.

Many constituents present in the human diet may inhibit endogenous formation of N-nitroso compounds (NOC). Studies with human volunteers showed inhibiting effects of intake of ascorbic acid and green tea consumption on nitrosation using the N-nitrosoproline test. The aim of the present study was to evaluate the effects of ascorbic acid and green tea on urinary excretion of carcinogenic N-nitrosodimethylamine (NDMA) and N-nitrosopiperidine (NPIP) in humans. Twenty-five healthy female volunteers consumed a fish meal rich in amines as nitrosatable precursors in combination with intake of nitrate-containing drinking water at the Acceptable Daily Intake level during 7 consecutive days. During 1 week before and after nitrate intake a diet low in nitrate was consumed. Using the same protocol, the effect of two different doses of ascorbic acid (250 mg and 1 g/day) and two different doses of green tea (2 g and 4 g/day) on formation of NDMA and NPIP was studied. Mean nitrate excretion in urine significantly increased from control (76+/-24) to 167+/-25 mg/24 h. Intake of nitrate and fish resulted in a significant increase in mean urinary excretion of NDMA compared with the control weeks: 871+/-430 and 640+/-277 ng/24 h during days 1-3 and 4-7, respectively, compared with 385+/-196 ng/24 h (p<0.0002). Excretion of NPIP in urine was not related to nitrate intake and composition of the diet. Intake of 250 mg and 1 g of ascorbic acid per day resulted in a significant decrease in urinary NDMA excretion during days 4-7 (p=0.0001), but not during days 1-3. Also, consumption of four cups of green tea per day (2 g) significantly decreased excretion of NDMA during days 4-7 (p=0.0035), but not during days 1-3. Surprisingly, consumption of eight cups of green tea per day (4 g) significantly increased NDMA excretion during days 4-7 (p=0.0001), again not during days 1-3. This increase is probably a result of catalytic effects of tea polyphenols on nitrosation, or of another, yet unknown, mechanism. These results suggest that intake of ascorbic acid and moderate consumption of green tea can reduce endogenous NDMA formation.

Volatile N-nitrosamine formation after intake of nitrate at the ADI level in combination with an amine-rich diet.

Formation of nitrite from ingested nitrate can result in several adverse health effects and implies a genotoxic risk as a consequence of endogenous formation of carcinogenic N-nitroso compounds. We studied the formation of volatile N-nitrosamines after intake of nitrate at the acceptable daily intake (ADI) level in combination with a fish meal rich in amines as nitrosatable precursors. Twenty-five volunteers consumed this meal during 7 consecutive days; a diet low in nitrate was consumed during 1 week before and 1 week after the test week. Nitrate intake at the ADI level resulted in a significant rise in mean salivary nitrate and nitrite concentrations. Mean urinary nitrate excretion increased from 76 mg/24 hr in the first control week to 194 and 165 mg/24 hr in the test week, followed by a decline to 77 mg/24 hr in the second control week. The urine samples were analyzed for volatile N-nitrosamines, and both N-nitrosodimethylamine (NDMA) and N-nitrosopiperidine (NPIP) were detected in the samples. Mean urinary NDMA excretion significantly increased from 287 ng/24 hr in the control week to 871 and 640 ng/24 hr in the test week and declined to 383 ng/24 hr in the second control week. Excretion of NPIP was not directly related to the nitrate intake and composition of the diet. Nitrate excretion and NDMA excretion were significantly correlated, as well as salivary nitrate and nitrite concentration and NDMA excretion. We conclude that nitrate intake at the ADI level in combination with a fish meal containing nitrosatable precursors increases NDMA excretion in urine and thus demonstrates increased formation of carcinogenic N-nitrosamines.

Formation of nitrosamines during consumption of nitrate- and amine-rich foods, and the influence of the use of mouthwashes.

We studied the formation of carcinogenic nitrosamines during consumption of food rich in nitrate and amines, and its possible inhibition by use of an antibacterial mouthwash. Twelve volunteers were fed a diet containing the high-nitrate vegetables lettuce or spinach during two periods of four consecutive days, in combination with fish products containing high levels of amines as nitrosatable precursors. During the two periods, the subjects used an antibacterial mouthwash containing chlorhexidine or a control mouthwash without antibacterial activity. Twenty-four-hour urine samples were collected after consumption of the meals, and saliva samples were collected 1 h after each meal. The nitrate and nitrite contents of the urine and saliva samples were determined by spectrophotometry (for nitrite) and HPLC (for nitrate). The concentrations of volatile nitrosamines in the urine samples were determined by gas chromatography-mass spectrometry. Significant increases in mean urinary nitrate levels (from 59 to 135 mg/24 h) and in mean salivary nitrate levels (from 10 to 56 microg/ml) and salivary nitrite levels (from 2 to 11 microg/ml) were observed during the consumption of food rich in nitrate and amines, as well as a significant increase in the mean urinary excretion of total examined volatile nitrosamines (from 2 to 7 nmol/24 h) and of N-nitrosodimethylamine (from 1.2 to 2.9 nmol/24 h). Use of the antibacterial mouthwash resulted in a decrease in mean salivary nitrite levels from 16 to 3 microg/ml and a decrease in mean urinary excretion of N-nitrosomorpholine (from 7.0 to 0.3 nmol/24 h). For the whole data set, significant correlations were observed between nitrate intake in food and urinary nitrate (p = 0.01; r2 = 0.07) and between urinary nitrate and urinary N-nitrosodimethylamine (p = 0.002; r2 = 0.11). In conclusion, consumption of a diet rich in nitrate and amines increases the risk of formation of carcinogenic nitrosamines. Use of an antibacterial mouthwash containing chlorhexidine can result in inhibition of nitrosamine formation.

Volatile N-nitrosamines in gastric juice of patients with various conditions of the gastrointestinal tract determined by gas chromatography-mass spectrometry and related to intragastric pH and nitrate and nitrite levels.

Gastric juice samples of 71 patients undergoing upper gastrointestinal endoscopy were collected as well as saliva samples from 40 of these patients. Age, sex, endoscopic diagnosis and medication were recorded. The gastric juice samples were analyzed for the presence and quantity of individual volatile N-nitrosamines, which were detected by gas chromatography-mass spectrometry, without prior derivatization. The samples were screened for eight nitrosamines, i.e. N-nitrosodimethylamine, N-nitrosoethylmethylamine, N-nitrosodiethylamine, N-nitrosodi-n-propylamine, N-nitrosodi-n-butylamine, N-nitrosopyrrolidine, N-nitrosopiperidine and N-nitrosomorpholine. The pH of the fresh gastric juice as well as nitrate and nitrite levels of gastric juice and saliva were determined. The mean total level of volatile N-nitrosamines in gastric juice was found to be 4.84 nmol/l (range 0-17.7 nmol/l). The main N-nitrosamines found were N-nitrosodiethylamine (mean concentration 3.1 nmol/l), N-nitrosodimethylamine (mean concentration 0.90 nmol/l) and N-nitrosopyrrolidine (mean concentration 0.38 nmol/l). Significant correlations between mean intragastric pH values and mean N-nitrosodi-n-butylamine level (P = 0.005) and total volatile N-nitrosamine contents (P = 0.009) were observed.

Nitrate contamination of drinking water: relationship with HPRT variant frequency in lymphocyte DNA and urinary excretion of N-nitrosamines.

We studied peripheral lymphocyte HPRT variant frequency and endogenous nitrosation in human populations exposed to various nitrate levels in their drinking water. Four test populations of women volunteers were compared. Low and medium tap water nitrate exposure groups (14 and 21 subjects) were using public water supplies with nitrate levels of 0.02 and 17.5 mg/l, respectively. Medium and high well water nitrate exposure groups (6 and 9 subjects) were using private water wells with mean nitrate levels of 25 and 135 mg/l, respectively. Higher nitrate intake by drinking water consumption resulted in a dose-dependent increase in 24-hr urinary nitrate excretion and in increased salivary nitrate and nitrite levels. The mean log variant frequency of peripheral lymphocytes was significantly higher in the medium well water exposure group than in the low and medium tap water exposure groups. An inverse correlation between peripheral lymphocyte labeling index and nitrate concentration of drinking water was observed. Analysis of N-nitrosamine in the urine of 22 subjects by gas chromatography-mass spectrometry revealed the presence of N-nitrosopyrrolidine in 18 subjects. Analysis of the mutagenicity of well water samples showed that a small number of the well water samples were mutagenic in the Ames Salmonella typhimurium test after concentration over XAD-2 resin. In conclusion, consumption of drinking water, especially well water, with high nitrate levels can imply a genotoxic risk for humans as indicated by increased HPRT variant frequencies and by endogenous formation of carcinogenic N-nitroso compounds from nitrate-derived nitrite.

Modulation of nitrate-nitrite conversion in the oral cavity.

The formation of nitrite from ingested nitrate can give rise to the induction of methemoglobinemia and endogenous nitrosation resulting in the formation of carcinogenic N-nitroso compounds. We investigated the possibility of modulation of the conversion of nitrate into nitrite in the oral cavity in order to seek ways of reducing the formation of the deleterious nitrite. We investigated the effectiveness of several mouthwash solutions with antibacterial constituents on the reduction of nitrate into nitrite in the oral cavity. In 15 studied subjects, the mean percentage of salivary nitrate reduced to nitrite after ingestion of 235 mg (3.8 mmol) nitrate was found to be 16.1 +/- 6.2%. The use of an antiseptic mouthwash with active antibacterial constituent chlorhexidine resulted in an almost complete decrease of the mean percentage of reduced nitrate, to 0.9 +/- 0.8%. Mouthwash solutions with antibacterial component triclosan or antimicrobial enzymes amyloglucosidase and glucose oxidase did not affect the reduction of nitrate into nitrite. A toothpaste with active components triclosan and zinc citrate with synergistic antiplaque activity was also without effect. Use of a pH-regulating chewing gum resulted in a rise in the pH in the oral cavity from 6.8 to 7.3. At 30 min after nitrate ingestion, this rise was accompanied by a significant increase in the salivary nitrite concentration, which might be explained by the pH being close to the optimal pH for nitrate reductase of 8. In conclusion, a limited number of possibilities of modulation of the conversion of nitrate into nitrite in the oral cavity are available.

Role of oxidative DNA damage in the mechanism of fecapentaene-12 genotoxicity.

Fecapentaene-12 (FP-12), a fecal unsaturated, ether-linked lipid excreted by most human individuals in Western populations, has been found to be a potent genotoxin in mammalian cells. Its mechanism of genotoxicity may be mediated by oxygen radical-induced DNA damage or by direct DNA alkylation, of which the relative importance remains to be determined. In the present study, induction of oxidative genetic damage by FP-12 has been investigated, in combination with the biological inactivation of single-stranded bacteriophage phi X-174 DNA. It was shown that formation of 7,8-dihydro-8-oxo-2'-deoxyguanosine (8-oxodG), a marker for oxidative DNA damage, is induced dose dependently by FP-12 in 2'-deoxyguanosine (dG). It was demonstrated by application of radical scavengers that production of both the superoxide anion and singlet oxygen may be involved in the induction of 8-oxodG. The effect of OH radical scavenging appeared to be less pronounced. Enzymatic peroxidation of FP-12, which has been demonstrated to stimulate oxygen radical formation, was found to increase the hydroxylation ratio in dG, an effect which was less pronounced in single-stranded DNA and even absent in double-stranded DNA. No induction of 8-oxodG was observed after exposure of human skin fibroblasts to 60 microM FP-12 for 3 h in vitro. It was concluded that the induction of 8-oxodG by FP-12 is determined by the accessibility of the guanine molecule rather than the rate of oxygen radical formation. Although free radical formation is known to be stimulated by enzymatic peroxidation of FP-12, the inactivation of phi X-174 DNA spontaneously induced by FP-12 was found to be reduced by application of peroxidases. This furthermore demonstrates that the increased formation of reactive oxygen species by enzymatic peroxidation of FP-12 does not directly relate to increased induction of genotoxic effects. The fact that addition of radical scavengers shows limited effects on the inactivation of phi X-174 DNA suggests that the contribution of oxidative DNA damage to the genotoxic potential of FP-12 is only of minor importance.

Formation of aromatic DNA adducts in white blood cells in relation to urinary excretion of 1-hydroxypyrene during consumption of grilled meat.

With the aim of studying the effect of oral exposure to polycyclic aromatic hydrocarbons (PAH) on human DNA-adduct formation in mononuclear cells and excretion of 1-hydroxypyrene in urine, we examined the effect of consumption of charcoal-broiled hamburgers. Hamburgers were grilled and samples were homogenized, saponified, extracted with hexane and analysed for PAH content by HPLC. The mean levels of benzo[a]pyrene and pyrene in the grilled hamburgers were 8.6 and 26.5 micrograms/kg respectively. Twenty one healthy non-smoking individuals consumed two hamburgers (170 g) per day for 5 days. 32P-Postlabelling analysis was performed on DNA samples of mononuclear cells of the subjects. The excretion of 1-hydroxypyrene in urine was studied as a marker of endogenous exposure to PAH. In the DNA samples of eight of the 21 subjects, on day 3 of the consumption period a predominant adduct spot could be detected with similar chromatographic properties to a benzo[a]pyrenediolepoxide--deoxyguanosine standard, the levels varying between 3 and 103 adducts/10(10) nucleotides. Analysis of the urine samples revealed maximal 1-hydroxypyrene excretion on day 3 in all nine subjects who collected urine daily during the consumption week, with an average level of 5.2 nmol/24 h. In a subsequent study in which six volunteers consumed charcoal-broiled hamburgers with lower levels of benzo[a]pyrene and pyrene, no aromatic DNA adducts in mononuclear cells or increased 1-hydroxypyrene levels in urine were detected. In conclusion, oral intake of PAH may dose-dependent induce elevated levels of aromatic DNA adducts in mononuclear cells and of 1-hydroxypyrene in urine, indicating substantial bioactivation of PAH, in particular via this route.

Peroxidation of linoleic, arachidonic and oleic acid in relation to the induction of oxidative DNA damage and cytogenetic effects.

In the present study, the possible role of the polyunsaturated fatty acids linoleic and arachidonic acid in the chemical induction of carcinogenesis has been investigated. Analysis of 7,8-dihydro-8-oxo-2'-deoxyguanosine (8-oxodG) levels in 2'-deoxyguanosine (dG) and isolated DNA has demonstrated that linoleic and arachidonic acid are capable of inducing this specific genotoxic damage. This effect appears to be related to the degree of fatty acid unsaturation, since it was not induced by monounsaturated oleic acid. Enzymatic peroxidation of linoleic and arachidonic acid resulted in a significant increase in oxidative DNA damage. Studies on the interference of radical scavengers with the induction of 8-oxodG in combination with electron spin resonance spectroscopy demonstrated that the superoxide anion was generated during peroxidation of these fatty acids and that singlet oxygen is most likely involved in the formation of oxidative DNA damage. The level of oxidative damage in dG and single-stranded DNA was higher as compared to that in native DNA after equimolar treatment. Exposure of human lymphocytes to linoleic or arachidonic acid did not result in a significant increase in levels of 8-oxodG. This may indicate that the rate of intracellular peroxidation is relatively low and/or that nuclear DNA in intact cells is effectively protected against genetic damage induced by reactive oxygen species. It is therefore concluded that relatively short periods of linoleic or arachidonic acid administration are not likely to impose a direct genotoxic risk. It can, however, not be excluded that chronic exposure to polyunsaturated fatty acids induces oxidative DNA damage or is related to cancer risk by epigenetic mechanisms, as is also indicated by the observed cytotoxic effects of linoleic and arachidonic acid.

Consumption of drinking water with high nitrate levels causes hypertrophy of the thyroid.

We studied the effect of nitrate contamination of drinking water on volume and function of the thyroid in human populations exposed to different nitrate levels in their drinking water. Two sets of low and medium (tap) water, respectively medium and high (well) water nitrate exposure groups were compared. Drinking of nitrate-contaminated water was dose-dependently related with 24-h urinary nitrate excretion and salivary nitrate levels. No iodine deficiency was observed in any of the nitrate exposure groups. A dose-dependent difference in the volume of the thyroid was observed between low and medium vs. high nitrate exposure groups, showing development of hypertrophy at nitrate levels exceeding 50 mg/l. An inverse relationship was established between the volume of the thyroid and serum thyroid stimulating hormone (TSH) levels.