Gene/Protein Disease Symptom Drug Enzyme Compound
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Query: DrugBank:APRD00249 (Mutagen)
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Differences greater than 6,000-fold in the mutagenic potency of three nitrosamides that are methylating agents [N-methyl-N-nitrosourea (MNU), N-methyl-N'-nitro-N-nitrosoguanidine (MNNG) and N-nitrosocarbaryl (NC)] could be accounted for in part by differences in their uptake into the Haemophilus influenzae cells. Uptake was roughly correlated with the octanol/water partition coefficient. The most potent mutagen, NC, was concentrated by the cells. The least potent, MNU, was essentially excluded from the bacteria. Uptake was a linear function of concentration, whereas induction of novobiocin-resistant mutations followed higher-order kinetics. The effective dose of chemical to the bacteria (number of molecules taken up) under conditions of mutagenesis could be calculated.
Environ Mutagen 1979
PMID:Mutagenicity of nitrosocarbaryl and other methylating nitrosamides as related to uptake in Haemophilus influenzae. 12 78

Plants have too long been ignored as useful screening and monitoring systems of environmental mutagens. However, there are about a dozen reliable, some even unique, plant genetic systems that can increase the scope and effectiveness of chemical and physical mutagen screening and monitoring procedures. Some of these should be included in the Tier II tests. Moreover, plants are the only systems now in use as monitors of genetic effects caused by polluted atmosphere and water and by pesticides. There are several major advantages of the plant test systems which relate to their reproductive nature, easy culture and growth habits that should be considered in mutagen screening and monitoring. In addition to these advantages, the major plant test systems exhibit numerous genetic and chromosome changes for determining the effects of mutagens. Some of these have not yet been detected in other nonmammalian and mammalian test systems, but probably occur in the human organism. Plants have played major roles in various aspects of mutagenesis research, primarily in mutagen screening (detection and verification of mutagenic activity), mutagen monitoring, and determining mutagen effects and mechanisms of mutagen action. They have played lesser roles in quantification of mutagenic activity and understanding the nature of induced mutations.Mutagen monitoring with plants, especially in situ on land or in water, will help determine potential genetic hazards of air and water pollutants and protect the genetic purity of crop plants and the purity of the food supply. The Tradescantia stamen-hair system is used in a mobile laboratory for determining the genetic effects of industrial and automobile pollution in a number of sites in the U.S.A. The fern is employed for monitoring genetic effects of water pollution in the Eastern states. The maize pollen system and certain weeds have monitored genetic effects of pesticides. Several other systems that have considerable value and should be developed and more widely used in mutagen monitoring and screening, especially for in situ monitoring, are discussed. Emphasis is placed on pollen systems in which changes in pollen structure, chemistry, and chromosomes can be scored for monitoring; and screening systems which can record low levels of genetic effects as well as provide information on the nature of induced mutations. THE VALUE OF PLANT SYSTEMS FOR MONITORING AND SCREENING MUTAGENS CAN BE IMPROVED BY: greater knowledge of plant cell processes at the molecular and ultrastructural levels; relating these processes to mutagen effects and plant cell responses; improving current systems for increased sensitivity, ease of detecting genetic and chromosome changes, recording of data (including automation), and for extending the range of genetic and chromosome end points; and designing and developing new systems with the aid of previous and current botanical and genetic knowledge.
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PMID:Potential of plant genetic systems for monitoring and screening mutagens. 36 68

Organic extracts of chlorinated Ontario drinking water samples have been found to induce mutation and lethality in the Salmonella/mammalian-microsome histadine reversion assay. Collections of water were made at water treatment plants in five municipalities in June 1978. To determine the reproducibility of the positive mutagenic effects found, a second sampling at the same plants was performed in September 1978. Preparation of extracts involved passing 200 liter samples through XAD-2 resin columns which were eluted with a mixture of hexane and acetone, and the eluent was evaporated to dryness. For those extracts with sufficient organic matter, dose-related increases in mutagenicity were observed. Extracts of untreated water from a river and a well were weakly mutagenic.
Environ Mutagen 1979
PMID:Mutagenicity of organic extracts from Canadian drinking water in the Salmonella/mammalian-microsome assay. 39 17

Paper recycling industries generate considerable quantities of waterborne wastes, and thus water pollution constitutes the greatest environmental problem associated with this industrial activity [Hunt and Franklin, 1973]. Generally the impact of this water pollution is considered in terms of aesthetic blight and deterioration of water quality. We present data that document another aspect of this pollution, the environmental contamination of an aquatic ecosystem with mutagenic materials. A natural population of the fern Osmunda regalis growing in a river heavily polluted with paper recycling wastes had a high incidence of chromosome mutations. This population was monitored for four years for the frequency of two-break chromosome mutations. These mutations were postzygotic in origin and suggested the presence of mutagens in the river water. The fern population is downstream from the outfalls of a paper recycling mill, which was discharging 13.3 X 10(6) liters of untreated paper recycling waste per day. In 1977 a waste-water-treatment facility was constructed to remove the solid waste previously discharged into the river. This facility generates 69,300 kg of solid waste daily, which is taken to a landfill. Periodic samples of this solid waste were collected from the waste-treatment facility in the summer of 1978, extracted with various solvents, and the extracts tested for mutagenic activity with the Salmonella/mammalian microsome mutagenicity test [Ames et al, 1975]. A majority of the solid waste samples contained mutagenic materials, but in all cases S-9 activation was required for mutagenic activity. The samples also were assayed with the soybean mitotic crossing-over assay [Vig, 1975]. Four out of six samples were positive. These results document the presence of mutagens in the solid waste generated by a paper recycling industry and the genetic impact of these mutagens on the local biota.
Environ Mutagen 1979
PMID:Mutagens in a river heavily polluted with paper recycling wastes: results of field and laboratory mutagen assays. 55 3

Bile flow and excretion of monohydroxy-, dihydroxy- and trihydroxy-bile acids (MBA, DBA and TBA) were estimated after acute and subacute phenobarbital and chlorpromazine pretreatment in 60-day-old male Wistar rats. Bile was collected in bile-fistula rats in three 1-hour periods. MBA were not detected. Neither single nor repeated ip. administration of different amounts of saline before bile sampling nor oral water supply within the bile collection period influenced the bile flow and excretion of DBA and TBA. Phenobarbital administration (60 mg/kg b.w. ip.) 2 hrs before bile sampling did not influence bile flow and bile acid (BA) excretion. After 3 days pretreatment with phenobarbital (3 X 60 mg/kg b.w. ip.) the bile flow was somewhat increased, BA-excretion was unchanged and the relation TBA/DBA diminished. Chlorpromazine administration (40 mg/kg b.w. ip.) 1,5 hrs before bile sampling decreased bile flow and BA excretion within the first collection period, whereas bile flow and BA excretion increased in the thrid collection period. No signs of cholestasis were observed after chlorpromazine pretreatment once a day for 3 days. Bile flow and BA excretion were increased and the relation TBA/DBA was unchanged.
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PMID:[Effect of phenobarbital and chlorpromazine on bile flow and bile acid excretion in male Wistar rats]. 70 25

In the halls of the pig fattening house the bactericidal effectiveness of cold water solutions of Czechoslovakia-made Jodofor A and the product of the Ciba-Geigy company Iosan was tested and compared with the effectiveness of Chloramin B used in a water solution at the temperature of 50 to 60 degrees C. The solutions were applied by fine spraying at the rate of 0.5 lt. per 1 m2 of area. After one hour the spray was applied again at the same rate. One hour after the last Jodofor spray and two hours after the last Chloramin B spray, smears were collected from the disinfected surfaces. The examination included the detection of coliform germs, germs of the Micrococcaceae family, and the determination of the total number of germs. On the whole, 384 smears were examined in four separate trials. The application of Jodofor A in 2% concentrations, after mechanical average-quality purification, did not give acceptable results, in comparison with the solution of Cloramin B. Only when solutions of Jodofor A and Iosan were used in 3% concentration after perfect mechanical purification, satisfactory results were obtained (with the exception of plaster and painted wood), in comparison with the Chloramin B solution. Better disinfectibility was found in aluminium sheet, terracotta, concrete, and metal, as distinct from plaster and painted wood. The comparison of Jodofor A with abroad-male Iosan indicates that Jodofor has the same or a better bactericidal effect than Iosan in all indices. Due to its bactericidal effect, Jodofor A is a suitable disinfectant for preventive disinfection of farm animal houses. In order to achieve results corresponding to those provided by 2% solutions of Chloramin B it is necessary to use at least 3% concentration of Jodofor A. Good mechanical purification is a basic prerequisite for its effectiveness.
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PMID:[Tests on the bactericidal effectiveness of iodophor A in the halls of a pig-fattening station]. 80 88

A laser Raman study of the alkylation of calf thymus DNA, poly(dG)-poly(dC) and poly(dA)-(dT) has been made using two water soluble alkylating agents: an antitumor drug, the difunctional methyl nitrogen mustard (HN2), which froms interstrand cross-links, and the dimethyl nitrogen half mustard (HN1). When an excess of the alkylating agent was used, the observed Raman frequencies due to the guanine ring modes in DNA and poly(dG)-poly(dC) changed virtually quantitatively to those of 7-methylguanosine (7-Me-Guo) showing that essentially all of the guanine bases were alkylated in the N-7 position. Furthermore, this alkylated DNA formed a stable double helical complex at neutral pH in which the alkylated guanine residues are in the keto form. No changes in the Raman bands of any of the other bases were observed in alkylated DNA. The DNA double helix, completely alkylated in at the N-7 position of guanine, melts about 35 degrees C below that of the native DNA. Upon melting, the alkylated guanine changes from the keto to the zwitterionic form.
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PMID:Detection of the sites of alkylation in DNA and polynucleotides by laser Raman spectroscopy. 93 35

The combination effects of bleomycin with N-nitrosoheptamethyleneimine (NHMI) or dihydroxy-di-N-propylnitrosamine (DHPN) on pulmonary carcinogenesis were investigated. Male F344 rats were given NHMI (20 or 40 ppm) or DHPN (200 ppm) in the drinking water and intraperitoneally injected with bleomycin (1 mg/kg) once a week for 18 weeks and then killed at week 24. Many rats treated with NHMI died before the termination of the experiment due to toxicity or development of advanced esophageal carcinomas, considered to be the main cause of death. Detailed histological examination performed on rats killed at week 24 revealed no statistically significant effects of bleomycin on NHMI or DHPN induction of neoplastic lesions in the lung or esophagus, although pulmonary carcinomas were only found in two rats treated with NHMI plus bleomycin. Under the present experimental conditions, NHMI exerted stronger carcinogenic activity in the esophagus than in the lung, and no obvious modifying effects of simultaneously administered bleomycin were evident on NHMI- or DHPN-induced pulmonary carcinogenesis.
Teratog Carcinog Mutagen 1992
PMID:N-nitrosoheptamethyleneimine-induced pulmonary and esophageal carcinogenesis and effects of concomitant treatment with bleomycin in rats. 128 78

An alkaline unwinding assay was used to quantitate the induction of DNA strand breaks (DNA SB) in the livers of rats and mice treated in vivo, in rodent hepatocytes in primary culture, and in CCRF-CEM cells, a human lymphoblastic leukemia cell line, following treatment with tri- (TCA), di- (DCA), and mono- (MCA) chloroacetic acid and their corresponding aldehydes, tri- (chloral hydrate, CH), di- (DCAA) and mono- (CAA) chloroacetaldehyde. None of the chloroacetic acids induced DNA SB in the livers of rats at 4 hr following a single administration of 1-10 mmole/kg. TCA (10 mmole/kg) and DCA (5 and 10 mmole/kg) did produce a small amount of strand breakage in mice (7% at 4 hr) but not at 1 hr. N-nitrosodiethylamine (DENA), an established alkylating agent and a rodent hepatocarcinogen, produced DNA SB in the livers of both species. TCA, DCA, and MCA also failed to induce DNA strand breaks in splenocytes and epithelial cells derived from the stomach and duodenum of mice treated in vivo. None of the three chloroacetaldehydes induced DNA SB in either mouse or rat liver. The continuous exposure of mice to 5 g/L DCA in the drinking water for 7 and 14 days did not induce appreciable hepatic DNA SB (< 10% at 14 days), although peroxisome proliferation, as evidenced by an increased cyanide-insensitive palmitoyl CoA oxidase (PCO) activity, was stimulated to 490% (7 days) and 652% (14 days) of control. Under this protocol, DENA (0.1 g/L) produced DNA damage after both 7 days (73% of control) and 14 days (57% of control). Similarly, long-term exposure of rats (30 weeks) to 2 g/L DCA in the drinking water, a level that increased PCO activity to 364% of the control value, exhibited no DNA damage. Both the chloroacetic acids and the chloroacetaldehydes were ineffective in inducing DNA SB in cultured rat and mouse hepatocytes at concentrations below those that yielded cytotoxicity. The chloroacetic acids were also ineffective in the CCRF-CEM cells. However, two of the chloroaldehydes, DCAA and CAA, did induce DNA SB in the CCRF-CEM cells at concentrations that did not decrease the cell viability after 2 hr of treatment. Prior incubation of DCAA and CAA with a rat S9 liver homogenate eliminated much of the DNA damaging activity. These studies provide further evidence that the chloroacetic acids lack genotoxic activity not only in rodent liver, a tissue in that they induce tumors, but in a variety of other roden tissues and cultured cell types.(ABSTRACT TRUNCATED AT 400 WORDS)
Environ Mol Mutagen 1992
PMID:Analysis of DNA strand breaks induced in rodent liver in vivo, hepatocytes in primary culture, and a human cell line by chlorinated acetic acids and chlorinated acetaldehydes. 133 May 47

Sodium/copper chlorophyllin (CHL) is a water-soluble derivative of chlorophyll that exhibits antimutagenic activity in several short-term genotoxicity assays and inhibits carcinogen-DNA binding in vivo. The effect of CHL pretreatment on the excretion of mutagens in the urine and feces of male Sprague-Dawley rats has been studied using the Salmonella mutagenicity assay. Animals were given 1 percent CHL in the drinking water for 2 days before administering a single dose of 2-amino-3-methylimidazo-[4,5-f]quinoline (IQ) by oral gavage. Rats pretreated with CHL had higher levels of mutagens in the urine and feces compared with animals given IQ alone; 48 hr after IQ administration, the total mutagenic dose excreted was < 4% in controls vs. 18% in rats given CHL. Mutagenicity required the presence of an activation system, was unaffected by treatment with beta-glucuronidase or arylsulfatase, and in both the urine and feces was accounted for by increased elimination of unmetabolized parent compound. The results support the view that CHL may operate in vivo as a "desmutagen" or interceptor molecule, interacting with IQ in the gut and tissues, and reducing carcinogen bioavailability.
Environ Mol Mutagen 1992
PMID:Chlorophyllin-enhanced excretion of urinary and fecal mutagens in rats given 2-amino-3-methylimidazo[4,5-f]quinoline. 139 10


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