Mechanism of action of antitumor drug etoposide: a review.

Metabolism studies of the antitumor drug etoposide show the formation of metabolites in the lactone ring, which are probably not important for the drug's mechanism of action, and oxidative transformations in the dimethoxyphenol ring (E ring), which lead to products that can cause DNA damage and may play a role in the drug's mechanism of action. The cytotoxicity of etoposide is caused by the induction of DNA damage. The occurrence of the DNA lesions can be explained by the capacity of the drug to interfere with the scission-reunion reaction of mammalian topoisomerase II by stabilizing a cleavable complex.

Cytochrome P-450-mediated O-demethylation: a route in the metabolic activation of etoposide (VP-16-213).

The antitumor agent VP-16-213 is oxidatively O-demethylated by rat liver microsomes and purified rat liver microsomal cytochrome P-450. 3-Methylcholanthrene can quantitatively induce O-demethylation of VP-16-213. The Km and Vmax values for O-demethylation by noninduced, phenobarbital-, and 3-methylcholanthrene-induced rat liver microsomes were found to be 130, 600, and 160 microM and 8.5, 11.8, and 15.6 nmol H2CO/min X mg protein, respectively. Mass spectrometric comparison of the product of O-demethylation of VP-16-213 with the synthetic metabolite resulted in identification of the orthodihydroxy derivative. In studies on the biological activity of the orthodihydroxy derivative, it was found to inactivate single- and double-stranded phiX174 DNA, to bind to calf thymus DNA and to be highly toxic against chinese hamster ovary cells.

5-Fluoro- and 5-chlorocyclophosphamide: synthesis, metabolism, and antitumor activity of the cis and trans isomers.

In seeking analogues of cyclophosphamide (1) having improved antitumor activity by virtue of accelerated formation of the cytotoxic metabolite phosphoramide mustard, cis and trans isomers of 5-fluoro- and 5-chlorocyclophosphamide (9, 10, 11 and 12, respectively) were synthesized by condensation of the appropriate 3-amino-2-halopropan-1-ol (13 or 26) with N,N-bis(2-chloroethyl)phosphoramidic dichloride (14). The metabolism of the halocyclophosphamides by rat liver microsomes was stereoselective; the cis isomers (9 and 11) were poorly metabolized, whereas the trans isomers (10 and 12) were metabolized with efficiency comparable to that of cyclophosphamide. However, there was no evidence that the yield of phosphoramide mustard produced by the trans analogues were significantly greater than that from cyclophosphamide following microsomal 4-hydroxylation. Hence, the halogen substituents did not accelerate beta-elimination of acrolein from the acyclic aldehydo tautomers. As expected, the poorly metabolized cis-5-fluoride (9) had little activity against the ADJ/PC6 tumor in mice. However, the cis-5-chloride (11) was as active as the trans isomer (12) and each had approximately half the therapeutic index of 1. The trans-5-fluoride (10) was much less active, having an ED90 value some 16-fold that of 1.

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.

One-electron reductive bioactivation of 2,3,5,6-tetramethylbenzoquinone by cytochrome P450.

Bioreductive activation of quinones in mammalian liver has generally been attributed to NADPH-cytochrome P450 reductase. However, in view of the 20-30-fold molar excess of cytochrome P450 over NADPH-cytochrome P450 reductase on the endoplasmic reticulum of the rat liver cell and the capability of cytochrome P450 to bind and reduce xenobiotics, it was considered of interest to investigate the possible role of cytochrome P450 in the bioreduction of quinones. In the present study, 2,3,5,6-tetramethyl-1,4-benzoquinone (TMQ) was chosen as a model quinone. First, TMQ was found to bind at the metabolic active site of phenobarbital (PB)-inducible cytochrome P450s of rat liver microsomes, indicating that TMQ is a potential substrate for cytochrome P450-mediated biotransformation. Second, with electron spin resonance, one-electron reduction of TMQ to a semiquinone free radical (TMSQ) was found to occur in these microsomal fractions. SK&F 525-A, a well-known inhibitor of cytochrome P450, strongly inhibited TMSQ formation in these subcellular fractions without affecting NADPH-cytochrome P450 reductase activity. One-electron reductive bioactivation of TMQ was further investigated with purified NADPH-cytochrome P450 reductase alone and in reconstituted systems of purified cytochrome P450-IIB1 and NADPH-cytochrome P450 reductase. As measured by ESR, purified cytochrome P450-IIB1 in the presence of NADPH-cytochrome P450 reductase was able to reduce TMQ to TMSQ at a much greater rate than in the presence of NADPH-cytochrome P450 reductase alone. Reduction of TMQ was also investigated by measuring the initial rate of NADPH oxidation by TMQ under anaerobic conditions. Inhibitors of cytochrome P450, namely SK&F 525-A and antibodies against PB-inducible cytochrome P450s, caused a substantial decrease in reductive metabolism in PB-treated microsomes. These antibodies were also effective in the inhibition of TMQ-induced NADPH oxidation in a complete reconstituted system of equimolar concentrations of cytochrome P450-IIB1 and NADPH-cytochrome P450 reductase, indicating that the reaction was specific for cytochrome P450-IIB1. Finally, initial rates of NADPH oxidation were determined in reconstituted systems containing varying amounts of NADPH-cytochrome P450 reductase and cytochrome P450-IIB1 to determine the contribution of either enzyme in the reduction of TMQ. As expected, NADPH-cytochrome P450 reductase was able to reduce TMQ to a small extent. However, reconstitution in the presence of increasing amounts of cytochrome P450-IIB1 (relative to NADPH-cytochrome P450 reductase) resulted in increasing rates of TMQ-induced NADPH oxidation.(ABSTRACT TRUNCATED AT 400 WORDS)

Formation of different reaction products with single- and double-stranded DNA by the ortho-quinone and the semi-quinone free radical of etoposide (VP-16-213).

In this report, the types of DNA damage introduced by the ortho-quinone and the semiquinone free radical of 4'-demethylepipodophyllotoxin-9-(4-6-O-ethylidene-beta-D- glucopyranoside) (etoposide) and their relevance for the inactivation of single-stranded (ss) and double-stranded (ds) replicative form (RF) phi X174 DNA have been examined in vitro. The ortho-quinone yielded in both ss and ds DNA only chemical adducts, of which on the average about 1 out of 3 and 1 out of 12 per DNA molecule led to inactivation of ss or RF phi X174 DNA, respectively. The semi-quinone free radical, on the other hand, generated both frank and alkali-labile strand-breaks in ss and in ds DNA which, however, did not contribute significantly to DNA inactivation. The radical introduced, in addition, chemical DNA adducts. Unlike the ortho-quinone adducts, however, each of the semi-quinone adducts was lethal in ss phi X174 DNA, while more than 40 were required for the inactivation of RF DNA. The excision repair system of Escherichia coli did not operate on semi-quinone-modified RF DNA but removed about half of the ortho-quinone adducts [van Maanen JMS, Lafleur MVM, Mans DRA, van den Akker E, de Ruiter C, Koostra PR, Pappie D, de Vries J, Retèl J and Pinedo HM, Biochem Pharmacol 37: 3579-3589, 1988]. When ortho-quinone-modified ss or ds DNA was subjected to a post-alkaline treatment, the adducts remained stably bound to the DNA and the degree of biological inactivation was not influenced. In contrast, post-alkaline treatment removed about 70 and 60% of the semi-quinone adducts from ss and ds DNA, respectively, which, in the case of ss phi X174 DNA, resulted in a partial restoration of the biological activity. It is concluded that the ortho-quinone and the semi-quinone free radical of etoposide produce different types of damage in DNA which have different effects on the biological activity.

Effects of the ortho-quinone and catechol of the antitumor drug VP-16-213 on the biological activity of single-stranded and double-stranded phi X174 DNA.

We have studied the effects of the recently reported two new metabolites of the antitumor agent VP-16-213, the ortho-dihydroxy derivative or catechol and the ortho-quinone, on the biological activity of single-stranded and double-stranded phi X174 DNA, the binding of the metabolites to calf thymus DNA and the conversion of the catechol into the ortho-quinone. Evidence was obtained for the oxidation of the catechol into the ortho-quinone and for the fact that the ortho-quinone is the metabolite of VP-16-213 responsible for its binding to rat liver microsomal proteins. The catechol and ortho-quinone of VP-16-213 were found to bind 7-9 times more strongly to calf thymus DNA than VP-16-213 itself. In contrast to the parent compound VP-16-213, the catechol as well as the ortho-quinone inactivated both single-stranded (ss) and double-stranded (RF) biologically active phi X174 DNA. The mean T37-values for inactivation of ss and RF phi X174 DNA by 2.2 x 10(-4)M catechol at 37 degrees and pH 7.4 were 96 and 640 min, respectively. Reduction of the ortho-quinone by NADPH cytochrome P-450 reductase resulted in formation of the catechol. The system ortho-quinone/NADPH cytochrome P-450 reductase inactivated ss phi X174 DNA with a mean T37-value of 454 min, and this inactivation was inhibited by DMSO. The mean T37-value for inactivation of ss phi X174 DNA by 1.8 x 10(-4) M ortho-quinone at 37 degrees and pH 4.0 was 24 min. The chemical stability of the ortho-quinone and the extent of inactivation of ss phi X174 DNA by the ortho-quinone were both pH-dependent: at higher pH the ortho-quinone was less stable and gave less inactivation of DNA. The aqueous decomposition product(s) of the ortho-quinone formed at pH 7.4 inactivated ss phi X174 DNA with a mean T37-value of 175 min. The rate of inactivation of RF phi X174 DNA by the ortho-quinone at pH 4.0 was twice as low as the rate of inactivation of ss phi X174 DNA: T37 = 49 min. When using excision repair deficient E. coli mutants (uvrA- or uvrC-), a higher inactivation of RF phi X174 DNA was found: T37 = 29 min for uvrA- E. coli, indicating that a part of the DNA damage introduced by the incubation with ortho-quinone is removed by excision repair.(ABSTRACT TRUNCATED AT 400 WORDS)

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.

Nitrate contamination of drinking water: evaluation of genotoxic risk in human populations.

Nitrate contamination of drinking water implies a genotoxic risk to man due to the endogenous formation of carcinogenic N-nitroso compounds from nitrate-derived nitrite. Thus far, epidemiological studies have presented conflicting results on the relation of drinking water nitrate levels with gastric cancer incidence. This uncertainty becomes of relevance in view of the steadily increasing nitrate levels in regular drinking water supplies. In an attempt to apply genetic biomarker analysis to improve the basis for risk assessment with respect to drinking water nitrate contamination, this study evaluates peripheral lymphocyte chromosomal damage in human populations exposed to low, medium, and high drinking water nitrate levels, the latter being present in private water wells. It is shown that nitrate contamination of drinking water causes dose-dependent increases in nitrate body load as monitored by 24-hr urinary nitrate excretion in female volunteers, but this appears not to be associated with peripheral lymphocyte sister chromatid exchange frequencies.

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.

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.

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.

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.

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.

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.