Genotoxicity of malachite green and leucomalachite green in female Big Blue B6C3F1 mice

Malachite green, a triphenylmethane dye used in aquaculture as an antifungal agent, is rapidly reduced in vivo to leucomalachite green. Previous studies in which female B6C3F1 mice were fed malachite green produced relatively high levels of liver DNA adducts after 28 days, but no significant induction of liver tumors was detected in a 2-year feeding study. Comparable experiments conducted with leucomalachite green resulted in relatively low levels of liver DNA adducts but a dose-responsive induction of liver tumors. In the present study, we fed transgenic female Big Blue B6C3F1 mice with 450 ppm malachite green and 204 and 408 ppm leucomalachite green (the high doses used in the tumor bioassays) and evaluated genotoxicity after 4 and 16 weeks of treatment. Neither malachite green nor leucomalachite green increased the peripheral blood micronucleus frequency or Hprt lymphocyte mutant frequency at either time point; however, the 16-week treatment with 408 ppm leucomalachite green did increase the liver cII mutant frequency. Similar increases in liver cII mutant frequency were not seen in the mice treated for 16 weeks with malachite green or in female Big Blue rats treated with a comparable dose of leucomalachite green for 16 weeks in a previous study [Mutat. Res. 547 (2004) 5]. These results indicate that leucomalachite green is an in vivo mutagen in transgenic female mouse liver and that the mutagenicities of malachite green and leucomalachite green correlate with their tumorigenicities in mice and rats. The lack of increased micronucleus frequencies and lymphocyte Hprt mutants in female mice treated with leucomalachite green suggests that its genotoxicity is targeted to the tissue at risk for tumor induction.     

In vivo genotoxicity of 2-amino-3,8-dimethylimidazo[4, 5-f]quinoxaline in lacI transgenic (Big Blue) mice

2-Amino-3,8-dimethylimidazo[4,5-f]quinoxaline (MeIQx), a heterocyclic amine found in cooked meat, is a strong mutagen in the Salmonella/microsome assay and was proven to be a hepatocarcinogen in rodents. We used the lacI transgenic (Big Blue(R)) mouse to investigate MeIQx genotoxicity in vivo. lacI mutant frequencies were examined in liver and colon after single intragastric administration of MeIQx (males) or 12 weeks of feeding in the diet (males and females). Micronucleus induction was monitored in the peripheral blood and cell proliferating activity was monitored by proliferating cell nuclear antigen (PCNA) immunostaining, but only after the intragastric administration. Intragastric treatment with MeIQx (100 mg/kg) did not increase mutant frequency (MF) in liver or colon but it did induce a slight but statistically significant increase in the incidence of micronucleated reticulocytes 48 h after the treatment. No apparent increase in PCNA-positive foci was observed in any of tissues analyzed 14 days after the treatment. Administration of MeIQx (300 ppm) in diet for 12 weeks, however, caused MF increases in liver and colon in male and female mice, with greater increases in the females. An increase was also obvious after 4 weeks, but only in females. The sex difference in MF is consistent with the fact that female mice are more susceptible to MeIQx carcinogenesis. These results demonstrated that in the transgenic mouse mutation assay, long-term feeding of MeIQx was more effective than single gastric exposures in revealing the compound's mutagenicity in the target organs of carcinogenicity and that sex differences in susceptibility can also be observed.     

Low dose genotoxicity of 2-amino-3,8-dimethylimidazo[4,5-f]quinoxaline (MeIQx) in gpt delta transgenic mice

Although humans are chronically exposed to most environmental chemicals at low doses, genotoxicity assays with rodents are usually performed at high doses with short treatment period. To investigate the dose-response of genotoxicity at lower doses, gpt delta transgenic mice were fed a diet containing 300, 30 or 3 parts per million (ppm) of 2-amino-3,8-dimethylimidazo[4,5-f]quinoxaline (MeIQx) for 12 weeks and the gpt mutations in the liver were analyzed. In addition, the mice were continuously fed a diet containing MeIQx at a dose of 300 ppm for 78 weeks to examine the effect of a long-term treatment. In the mice treated for 12 weeks, the gpt mutant frequencies (MFs) were 8.6-, 2.3- and 1.2-fold higher than the control level at the doses of 300, 30 and 3 ppm, respectively. G:C to T:A transversion was the most predominant type of mutations and the fold increases in the specific MF of G:C to T:A were 58.2, 4.4 and 1.7 above the control at the three doses, respectively. The increases in the whole gpt and specific MFs at 3 ppm were not statistically significant. In the mice treated with 300 ppm of MeIQx for 78 weeks, the gpt MF was about 20 times higher than that of the untreated mice fed a control diet for 78 weeks, which was about two times higher than that of the untreated mice at 12 weeks. These results suggest that no obvious genotoxic effects can be detectable at the dose of MeIQx at 3 ppm in the liver and a longer treatment substantially enhances the genotoxicity. Factors constituting the practical threshold dose are discussed.     

Subchronic administration of phenobarbital alters the mutation spectrum of lacI in the livers of Big Blue transgenic mice

Phenobarbital (PHE) is a liver carcinogen in B6C3F1 mice and a weak mutagen that does not appear to form DNA adducts. To investigate PHE mutagenicity in vivo, B6C3F1 Big Blue(R) male transgenic mice harboring the lambdaLIZ shuttle vector containing the lacI target gene were fed PHE at 2500 ppm for 180 days. A modest increase in the mutant frequency (MF) from 5.02+/-2.4x10(-5) in the control group to 6.88+/-0.754x10(-5) in the PHE-treated group, which was marginally different (p<0.05), was obtained. To better assess the relevance of this increase in MF, a random collection of mutants from each PHE-exposed mouse was sequenced. After correcting for clonal expansion, which is the most conservative approach, the MF in the PHE-treated mice decreased to 6.39+/-1.02x10(-5), an insignificant difference (p=0.10) from that in control group. Despite this modest increase in MF, the mutation spectrum obtained from the PHE-exposed group was significantly different (pA:T transitions remained the same in the two spectra. It is postulated that the increase in transversions at G:C base pairs found in the PHE-derived spectrum is likely due to oxidative damage as a result of induction of CYP2B isozymes by the chronic administration of PHE. Results from this study demonstrate that PHE alters the spectrum of mutations, rather than inducing a significant global increase in the MF. The PHE-derived spectrum of lacI mutants from the liver of Big Blue(R) B6C3F1 male mice was remarkably similar (p=0.8) to that generated by oxazepam (OX), a compound which also induces CYP2B isozymes following chronic administration of the drug.     

Mutagenicity of 1,3-butadiene at the Hprt locus of T-lymphocytes following inhalation exposures of female mice and rats.

The species specific response to 1,3-butadiene (BD), an important industrial chemical, was investigated by determining the influence of exposure duration and exposure concentration on the mutagenicity of BD in mice and rats and by defining the spectra of mutations in the Hprt gene T-cell mutants from control and BD-exposed mice. Female B6C3F1 mice and F344 rats (4-5 weeks old) were exposed by inhalation to 0, 20, 62.5, or 625 ppm of BD for up to 4 weeks (6 h/day, 5 days/week). Groups of control and exposed animals (n=4-12/group) were necropsied at multiple time points after exposure and the T-cell cloning assay was used to measure Hprt mutant frequencies in lymphocytes isolated from spleen. Mutant clones collected from control and BD-exposed mice were propagated and analyzed by RT-PCR to produce Hprt cDNA for sequencing. In animals necropsied 4 weeks after 2 or 4 weeks of BD exposure (0 or 625 ppm), the rate of accumulation of mutations was greater in mice than in rats. Supra-linear dose-response curves were observed in BD-exposed mice, indicating a higher efficiency of mutant induction at lower concentrations of BD. The mutagenic potency estimates (represented by the differences in the areas under the mutant T-cell 'manifestation' curves of treated vs. control animals) in mice were 11 and 61 following 4 weeks of exposures to 62.5 and 625 ppm of BD, respectively, while mutant frequencies (Mfs) in rats were significantly increased only at 625 ppm BD (mutagenic potency of 7). Molecular analysis of Hprt cDNA from expanded T-cell clones from control and BD-exposed mice demonstrated an increased frequency of mutants in exposed animals that likely contain large deletions in the Hprt gene (P=0.016). These data indicate that both exposure duration and exposure concentration are important in determining the magnitude of mutagenic response to BD, and that mutagenic and carcinogenic properties of BD in mice may be related more to the ability of its metabolites to cause chromosomal deletions than to produce point mutations.     

Aflatoxin B1-induced Hprt mutations in splenic lymphocytes of Fischer 344 rats. Results of an intermittent feeding trial

In a previous study, we found an increase in the mutant frequency at the Hypoxanthine phosphoribosyl transferase (Hprt) locus in the splenic lymphocytes of Fischer 344 rats acutely exposed to aflatoxin B1 (AFB1). Because an acute exposure may not reflect the exposure pattern of individuals whose diet may contain AFB1-contaminated foodstuffs, we sought to determine if the feeding regimen affected the induction of Hprt mutations in the rat splenic lymphocyte. Thus, Fischer 344 rats were fed either (A) a control diet, (B) various doses of AFB1 for three four-week periods interspersed with two four-week periods of the control diet, or (C) continuously fed 1.6 ppm of AFB1. Not only was a significant increase in the mutant frequency detected in the lymphocytes of rats fed a dose as low as 0. 01 ppm of AFB1, but the increase in the mutant frequency at the end of the 20-week experimental period was consistent with an accumulation of damage induced by AFB1. These results indicate that the rat lymphocyte/Hprt assay is useful for detecting chronic low level exposures. Further, these data suggest that an intermittent, low-level exposure to AFB1 may present a human health risk.     

1,3-Butadiene: Biomarkers and application to risk assessment

1,3-Butadiene (BD) is a known rodent and human carcinogen that is metabolized mainly by P450 2E1 to three epoxides, 1,2-epoxy-3-butene (EB), 1,2:3,4-diepoxybutane (DEB) and 1,2-epoxy-3,4-butanediol (EB-diol). The individual epoxides vary up to 200-fold in their mutagenic potency, with DEB being the most mutagenic metabolite. It is important to understand the internal formation of the individual epoxides to assign the relative risk for each metabolite and to understand the molecular mechanisms responsible for major species differences in carcinogenicity. We have conducted extensive exposure-biomarker studies on mice, rats and humans. Using low exposures that range from current occupational levels to human exposures from tobacco smoke has provided evidence that mice are very different from humans, with mice forming ～200 times more DEB than humans at exposures of 0.1-1.5ppm BD. While no gender differences have been noted in mice and rats for globin adducts or N-7 guanine adducts, female rats and mice had 2-3-fold higher Hprt mutations and DNA-DNA cross-links, suggesting a gender difference in DNA repair. Numerous molecular epidemiology studies have evaluated globin adducts and Hprt mutations, SCEs and chromosomal abnormalities. None of the blinded studies have shown evidence of human genotoxicity at current occupational exposures and studies of globin adducts have shown similar or lower formation of adducts in females than males. If one calculates the EB dose-equivalents for the three species, mice clearly differ from rats and humans, being ～44 and 174 times greater than rats and humans, respectively. These data provide a scientific basis for improved risk assessment of BD.     

Mutagenesis by man-made mineral fibres in the lung of rats

The potential of two asbestos substitute mineral fibres--rock (stone) wool RW1 and glass wool MMVF10--to induce gene mutations, DNA strand breaks, inflammation and oxidative stress has been studied in rats. Male homozygous lamda-lacI transgenic F344 rats were intratracheally instilled with single doses of 1 and 2 mg/animal of fibres or with multiple doses of 2 mg/animal administered weekly on four consecutive weeks (8 mg in total). Exposure to RW1 fibres for 16 weeks significantly increased mutant frequency (MF) in the lung in a dose-dependent manner, while MMVF10 fibres did not exhibit any increase of MF at any dose. RW1 fibres gave a significant increase of MF at a dose of 1 mg. Four weeks after instillation, neither the single nor the multiple doses significantly increased MF for both fibre types. To investigate mechanisms for induction of mutations, other genotoxicity markers and parameters of inflammatory and oxidative damage were determined in relation to MF. A weak correlation of mutagenicity data with other genotoxicity parameters studied was observed. DNA strand breaks as measured by comet assay were increased in alveolar macrophages and lung epithelial cells of RW1 and MMVF10 treated rats. RWl fibres caused more extensive lung inflammation as measured by release of neutrophils into broncho-alveolar lavage fluid than MMVF10 fibres. The effects were observed 16 weeks post-exposure, indicating a persistence of the pathogenic process during the exposure period. Only minor differences in the extent of inflammatory processes were observed between the doses of 2 mg and 4 x 2 mg, suggesting that any threshold for inflammation lies below the dose of 2 mg. With the exception of the highest dose of MMVF10 fibres after 16 weeks of exposure, no significant increase of oxidative damage as measured by levels of malondialdehyde in lung tissue was observed. MMVF10 fibres caused weaker inflammation in the lung of rats and did not exhibit any mutagenic effect. We conclude that a weak but chronic inflammation (more likely than acute inflammation or direct oxidative damage) in the lung tissue of fibre treated rats characterized by moderate influx of inflammatory cells into BAL is probably responsible for the observed mutagenic effect of RW1 fibres.     

Formation of DNA adducts and induction of mutagenic effects in rats following 4 weeks inhalation exposure to ethylene oxide as a basis for cancer risk assessment

Ethylene oxide (EO) is mutagenic in various in vitro and in vivo test systems and carcinogenic in rodents. EO forms different adducts upon reaction with DNA, N7-(2-hydroxyethyl)guanine (N7-HEG) being the main adduct. The major objectives of this study were: (a) to determine the formation and persistence of N7-HEG adducts in liver DNA of adult male rats exposed to 0, 50, 100 and 200 ppm by inhalation (4 weeks, 5 days/week, 6 h/day) and (b) to assess dose-response relationships for Hprt gene mutations and various types of chromosomal changes in splenic lymphocytes.N7-HEG adducts were measured 5, 21, 35 and 49 days after cessation of exposure. By extrapolation, the mean concentrations of N7-HEG immediately after cessation of exposure ('day 0') to 50, 100 and 200 ppm were calculated as 310, 558 and 1202 adducts/10(8) nucleotides, respectively, while the mean concentration in control rats was 2.6 adducts/10(8) nucleotides. At 49 days, N7-HEG values had returned close to background levels. The mean levels of N-(2-hydroxyethylvaline) adducts in haemoglobin were also determined and amounted 61.7, 114 and 247 nmol/g globin, respectively. Statistically significant linear relationships were found between mean N7-HEG levels ('day 0') and Hprt mutant frequencies at expression times 21/22 and 49/50 days and between mean N7-HEG ('day 0') and sister-chromatid exchanges (SCEs) or high frequency cells (HFC) measured 5 days post-exposure. At day 21 post-exposure, SCEs and HFCs in-part persisted and were significantly correlated with persistent N7-HEG adducts. No statistically significant dose effect relationships were observed for induction of micronuclei, nor for chromosome breaks or translocations.In conclusion, this study indicates that following sub-chronic exposure, EO is only weakly mutagenic in adult rats. Using the data of this study to predict cancer risk in man resulting from low level EO exposures in conjunction with other published data, i.e., those on (a) genotoxic effects of EO in humans and rats, (b) DNA binding of other carcinogens, (c) natural background DNA binding and (d) genotoxic potency of low energy transfer (LET) radiation, it is not expected that long term occupational exposure to airborne concentrations of EO at or below 1 ppm EO produces an unacceptable increased risk in man.     

Genotoxicity of furan in Big Blue rats

Furan is a multispecies liver carcinogen whose cancer mode of action (MOA) is unclear. A major metabolite of furan is a direct acting mutagen; however, it is not known if genotoxicity is a key step in the tumors that result from exposure to furan. In order to address this question, transgenic Big Blue rats were treated by gavage five times a week for 8 weeks with two concentrations of furan used in cancer bioassays (2 and 8mg/kg), and with two higher concentrations (16 and 30mg/kg). Peripheral blood samples taken 24h after the 5th dose (1 week of dosing) were used to assay for micronucleus (MN) frequency in normochromatic erythrocytes (NCEs) and reticulocytes (RETs), and Pig-a gene mutation in total red blood cells (RBCs). 24h after the last dose of the 8-week treatment schedule, the rats were euthanized, and their tissues were used to perform NCE and RET MN assays, the Pig-a RBC assay, Pig-a and Hprt lymphocyte gene mutation assays, the liver cII transgene mutation assay, and the liver Comet assay. The responses in the MN assays conducted at both sampling times, and all the gene mutation assays, were uniformly negative; however, the Comet assay was positive for the induction of liver DNA damage. As the positive responses in the Comet assay were seen only with doses in excess of the cancer bioassay doses, and at least one of these doses (30mg/kg) produced toxicity in the liver, the overall findings from the study are consistent with furan having a predominantly nongenotoxic MOA for cancer.     

Age-, gender-, and species-dependent mutagenicity in T cells of mice and rats exposed by inhalation to 1,3-butadiene

Experiments were performed: (i) to investigate potential age- and gender-dependent differences in mutagenic responses in T cells following exposures of B6C3F1 mice and F344 rats by inhalation for 2 weeks to 0 or 1250 ppm butadiene (BD), and (ii) to determine if exposures for 2 weeks to 62.5 ppm BD produce a mutagenic effect in female rats. To evaluate the effect of age on mutagenic response, mutant manifestation curves for splenic T cells of female mice exposed at 8-9 weeks of age were defined by measuring Hprt mutant frequencies (MFs) at multiple time points after BD exposure using a T cell cloning assay and comparing the resulting mutagenic potency estimate (calculated as the difference of areas under the mutant manifestation curves of treated versus control animals) to that reported for female mice exposed to BD in the same fashion beginning at 4-5 weeks of age. The shapes of the mutant T cell manifestation curves for spleens were different [e.g., the maximum BD-induced MFs in older mice (8.0+/-1.0 [S.D.]x10(-6)) and younger mice (17.8+/-6.1 x 10(-6)) were observed at 8 and 5 weeks post-exposure, respectively], but the mutagenic burden was the same for both age groups. To assess the effect of gender on mutagenic response, female and male rodents were exposed to BD at 4-5 weeks of age and Hprt MFs were measured when maximum MFs are expected to occur post-exposure. The resulting data demonstrated that the pattern for mutagenic susceptibility from high-level BD exposure is female mice>male mice>female rats>male rats. Exposures of female rats to 62.5 ppm BD caused a minor but significant mutagenic response compared with controls (n=16/group; P=0.03). These results help explain part of the differing outcomes/interpretations of data in earlier Hprt mutation studies in BD-exposed rodents.     

Sucrose and IQ induced mutations in rat colon by independent mechanism

Sucrose-rich diets have repeatedly been observed to have co-carcinogenic actions in colon and liver of rats and to increase the number of 2-amino-3-methylimidazo[4,5-f]quinoline (IQ) induced aberrant crypt foci in rat colon. To investigate a possible interaction between sucrose and IQ on the genotoxicity in rat liver and colon, we gave Big Blue rats a diet containing sucrose (0%, 3.45% or 13.4% w/w) and/or IQ (70 ppm) for a period of 3 weeks. Sucrose and IQ increased the mutation frequency in the colon. The effect of combined treatments with IQ and sucrose on the mutation frequencies was additive indicating that sucrose and IQ act independently. This was supported by the mutation spectra where sucrose expands the background mutations in the colon, whereas IQ, in other studies, more specifically has induced G:C --> T:A transversions. In the liver IQ increased the mutation frequency, whereas addition of sucrose reduced the effect of IQ in a dose-dependent manner. The level of bulky DNA adducts in liver and colon was increased in animals exposed to either sucrose or IQ. In animals exposed to IQ, addition of sucrose had marginal effects on the level of bulky DNA adducts. Markers of oxidative damage and DNA repair were generally unaffected by the treatments. In conclusion, sucrose and IQ in the diet induced mutations in the colon by independent mechanisms, whereas an interaction was observed in liver leading to a decrease in mutations by the combined treatment.     

Dietary low-dose sucrose modulation of IQ-induced genotoxicity in the colon and liver of Big Blue rats

Earlier studies have indicated that sucrose increases 2-amino-3-methylimidazo[4,5-f]quinoline (IQ)-induced aberrant crypt foci in the colon. In this study, we investigated the role of sucrose in IQ-induced genotoxicity of the colon mucosa and liver. Big Blue rats were fed with IQ (20 ppm in feed) and/or sucrose (3.45 or 6.85 wt.% in feed) for 3 weeks. IQ increased DNA strand breaks in the colon, whereas the mutation frequency was increased in the liver. The level of IQ-induced DNA adducts was elevated in both colon mucosa cells and liver. In the liver, high sucrose intake increased the level of DNA adducts above that of IQ and low sucrose intake. Oxidative DNA damage detected in terms of 7-hydro-8-oxo-2'-deoxyguanosine by HPLC-EC, or endonuclease III or formamidopyrimidine DNA glycosylase sensitive sites were unaltered in the colon and liver. Expression of ERCC1 and OGG1 mRNA levels were unaffected by IQ or sucrose feeding. Biomarkers of oxidative stress, including Vitamin C, malondialdehyde and protein oxidations (gamma-glutamyl semialdehyde and 2-amino adipic semialdehyde) were unaltered in plasma and in liver. In conclusion, sucrose feeding increases IQ-induced genotoxicity in liver but not in colon, suggesting different mechanisms for sucrose and IQ in colon mutagenesis.     

The effect of high fluoride intake on tissue trace elements and histology of testicular tubules in the rat

1. Male Wistar rats were exposed to fluoride (F) at concentrations of 100- and 200 ppm in their drinking water for 6- and 16 weeks.2. The high F intake caused several-fold increase in the F concentrations in the testes and bone as compared with control rats, both after the 6- and 16wk exposure; the bone F, but not testicular F, appeared to increase with dose and time.3. F exposure (100- and 200 ppm) decreased significantly the concentrations of zinc (Zn) in the testes, plasma, liver and kidneys particularly in the 16 wk groups; in the bone Zn tended to increase, however.4. The iron concentrations of the testes and plasma were not affected by F, whereas those of the liver, kidneys and bone appeared to increase under the influence of F.5. The concentrations of copper and manganese in the testes, liver and kidneys were not changed by F exposure.6. Fifty percent of the 100- and 200 ppm F rats after 16 weeks exhibited histopathologic changes in the germinal epithelium of the testes, which resembled those in Zn-deficient rats.7. The data suggest that a deprivation of testicular Zn due to a high F intake may be directly responsible for the injury of testicular tubules.     

浸泡条件下孔雀石绿及其代谢物隐色孔雀石绿在斑点叉尾 组织中分布及消除规律研究

以7 mg/L的孔雀石绿浸泡斑点叉尾 苗种5min后将其饲养于池塘的网箱中, 研究了在养殖模式下孔雀石绿及其代谢物隐色孔雀石绿在斑点叉尾 苗种各组织中的分布及消除规律。采用高效液相色谱串联质谱法(HPLC-MS/MS)分析孔雀石绿及其代谢物隐色孔雀石绿在斑点叉尾 血液、肌肉、皮肤、肝脏、肾脏组织中的浓度水平。采用药代动力学分析软件3p97对血药浓度时间数据进行分析。结果表明, 孔雀石绿和隐色孔雀石绿血药浓度时间曲线符合有吸收二室模型, 动力学方程分别为: C孔雀石绿 =683.063 e-0.248 t+ 11.176 e-0.006 t- 694.239e-0.333 t, C隐色孔雀石绿 =757.240 e-0.222 t + 14.474 e-0.007 t 771.714 e-0.382 t。血液中孔雀石绿和隐色孔雀石绿达峰时间Tpeak分别为3.480和3.623h, 峰浓度值Cmax分别为81.560和159.619 ng/mL, 表观分布容积Vd/F分别为37.689和21.125 L/kg, 分布相的一级速率常数分别为0.248和0.222/h, 消除相的一级速率常数分别为 0.006和0.007/h, 吸收半衰期T(1/2) 分别为2.794和3.124h, 消除半衰期T(1/2)分别为113.068和105.841h, 中央室向周边室转运的一级速率常数K12分别为0.020和0.015/h, 周边室向中央室转运的一级速率常数K21分别为0.159和0.121/h, 药-时曲线下面积AUC分别为2493.944和3601.863 ngh/mL。肌肉、皮肤、肝脏和肾脏组织中孔雀石绿和隐色孔雀石绿浓度水平的结果表明, 孔雀石绿在斑点叉尾 4种组织中浓度由高到低的顺序是皮肤肌肉肾脏肝脏, 其中斑点叉尾 皮肤组织易蓄积孔雀石绿, 其残留时间最长, 肝脏组织由于对孔雀石绿有极强的代谢转化功能而浓度较低。孔雀石绿在肌肉、皮肤、肝脏和肾脏组织中的消除方程分别为C=5.570 e-0.009t、C=6.302 e-0.007t、C=4.791 e-0.006t和C=4.591 e-0.002t, 相关系数r20.773, 消除半衰期T1/2肌肉、皮肤、肝脏和肾脏分别为3.2、4.1、4.8和14.4d。肌肉、皮肤、肝脏和肾脏组织中孔雀石绿分别在45、60、30和60d才未被检测到; 隐色孔雀石绿在斑点叉尾 4种组织中浓度由高到低的顺序是肝脏皮肤肌肉肾脏, 残留时间最长的组织也是皮肤组织。隐色孔雀石绿在肌肉、皮肤、肝脏和肾脏组织中的消除方程分别为C=6.491 e-0.004t、C=6.958 e-0.003t、C=6.722 e-0.007t和C=6.162 e-0.002t, 相关系数r20.673, 消除半衰期T1/2肌肉、皮肤、肝脏和肾脏分别为7.2、9.6、4.1和14.4d。肌肉、皮肤、肝脏和肾脏组织中隐色孔雀石绿分别在90、90、60和90d才未被检出。试验期间(2011年5月17日至7月15日)平均水温为26.4℃, 孔雀石绿和隐色孔雀石绿90d后在各组织中才未检测到, 因此, 使用7 mg/L孔雀石绿浸泡2龄斑点叉尾 苗种孔雀石绿及其代谢物隐色孔雀石绿至少应经过2376℃d后才能消除。       

Dose-dependent reduction of 3,2'-dimethyl-4-aminobiphenyl-derived DNA adducts in colon and liver of rats administered celecoxib

Colon cancer is second leading cause of cancer-related deaths in Western countries. Diet and smoking, which contain aromatic and heterocyclic amines, are major risk factors for colon cancer. Colorectal cancers have a natural history of long latency and therefore provide ample opportunities for effective chemoprevention. 3,2'-Dimethyl-4-aminobiphenyl (DMABP) is an experimental aromatic amine that causes cancer in rat colon and serves as an experimental model for arylamine and heterocyclic amine mutagens derived from diet and smoking. In this study, we investigated the effects of celecoxib, a selective cyclooxygenase-2 (COX-2) inhibitor on DMABP-induced DNA adduct formation in rat liver and colon. Male F-344 rats (5-week old) were provided free access to modified AIN-76A rat chow containing 0 (control), 500, 1000, or 1500 ppm celecoxib. Two weeks later, the rats received a subcutaneous injection of 100mg/kg DMABP in peanut oil. Two days after DMABP treatment, the rats were killed and DMABP-derived adducts were analyzed in colon and liver DNA by butanol extraction-mediated (32)P-postlabeling. Two major DNA adducts, identified as dG-C8-DMABP and dG-N(2)-DMABP, were detected in liver and colon of rats treated with DMABP. These DNA adducts were diminished approximately 35-40% with 500 ppm and 65-70% with 1,000 ppm celecoxib. In the colon, no further decline in DNA adducts was observed at 1500 ppm. The same DMABP-DNA adducts also were detected in the liver and were also diminished by celecoxib treatment. The reduction in DMABP-DNA adduct levels in celecoxib-treated animals provides further support for celecoxib as a chemopreventive agent for colorectal cancer.     

Mutagenicity of the racemic mixtures of butadiene monoepoxide and butadiene diepoxide at the Hprt locus of T-lymphocytes following inhalation exposures of female mice and rats.

The purpose of this study was to determine if Hprt mutant frequency (Mf) data from rodents exposed directly to individual epoxy metabolites of 1,3-butadiene (BD) can be used to identify the relative significance of each intermediate in the mutagenicity of BD in mice vs. rats. To this end, the relative contributions of the racemic mixtures of BD monoepoxide (BDO) and BD diepoxide (BDO(2)) to BD-induced mutagenicity was investigated by exposing mice and rats to selected concentrations of BDO and BDO(2) (i.e., 2.5 and 4.0 ppm, respectively) and comparing the mutagenic potency of each intermediate to that of BD (at 62.5 ppm) when comparable blood levels of metabolites are achieved (in the mouse). Female B6C3F1 mice and F344 rats (4-5 weeks old) were exposed to rac-BDO (0, 2.5, or 25 ppm) or (+/-)-BDO(2) (0, 2, 4 ppm) by inhalation for 4 weeks (6 h/day, 5 days/week), and then groups of control and exposed animals (n=3-12/group) were necropsied at multiple time points post-exposure for measuring Hprt Mfs in splenic lymphocytes (via the T-cell cloning assay) and estimating mutagenic potencies (represented by the difference in the areas under the mutant T-cell 'manifestation' curves of treated vs. control animals). The resulting Mf data, along with the extant metabolism data, suggest that at lower BD exposures (相似文献   

Effects of 1,4-phenylenebis(methylene)selenocyanate on mutagenesis and p53 protein expression in the tongue of lacI rats treated with 4-nitroquinoline-N-oxide

Previously we showed that the organoselenium compound, 1,4-phenylenebis(methylene)selenocyanate (p-XSC)(1) inhibits 4-nitroquinoline-N-oxide (4-NQO)-induced tongue tumorigenesis in Fisher rats. Here we investigate possible mechanisms of this inhibition by monitoring mutagenesis and p53 protein levels in lacI and conventional Fisher rats treated with: (1) a carcinogenic dose of 4-NQO for 10 weeks in drinking water, (2) 4-NQO+p-XSC (15 ppm as selenium), and (3) 4-NQO followed by p-XSC. For mutagenesis studies, rats were euthanized at 7, 12 or 23 weeks after the start of 4-NQO. For studies on p53 levels, rats were euthanized at 11, 15 and 23 weeks. Appropriate controls were also monitored. In the 4-NQO-alone groups, the mutant fraction (MF) in the cII gene in tongue increased at least 50x background level. The MF (in units of mutants/10(5) plaque forming units) for the 7, 12, and 23 weeks 4-NQO groups were respectively, 184 +/- 88, 237 +/- 105, and 329 +/- 110. Thus, mutagenesis increased with length of exposure and post-treatment time. p-XSC modestly (ca. 15-30%) inhibited mutagenesis under all conditions. The inhibition reached significance at the last time point. When p-XSC was administered after 4-NQO, the MF was also modestly reduced. In 4-NQO-alone animals, levels of p53 in tongue (determined by Western blotting) were 1, 1.5 and 2.4 control levels at 10, 15 and 23 weeks, respectively. In the p-XSC+4-NQO group, the enhancement in p53 levels by 4-NQO treatment was decreased about 90% at 15 weeks and 45% (P<0.05) at 23 weeks, and by slightly smaller percentages in corresponding post-treatment groups. p-XSC alone did not alter p53 levels. As p53 levels generally increase in response to DNA damage, these results suggest that p-XSC reduces 4-NQO-induced DNA damage, resulting in reduced 4-NQO-induced mutagenesis and carcinogenesis. However, the fact that p-XSC is also effective when administered after 4-NQO, suggests additional mechanisms of inhibition exist.     

Measurement of plasma or urinary metabolites and Hprt mutant frequencies following inhalation exposure of mice and rats to 3-butene-1,2-diol

Studies were performed to determine if the detoxification pathway of 1,3-butadiene (BD) through 3-butene-1,2-diol (BD-diol) is a major contributor to mutagenicity in BD-exposed mice and rats. First, female and male mice and rats (4-5 weeks old) were exposed by nose-only for 6h to 0, 62.5, 200, 625, or 1250 ppm BD or to 0, 6, 18, 24, or 36 ppm BD-diol primarily to establish BD and BD-diol exposure concentrations that yielded similar plasma levels of BD-diol, and then animals were exposed in inhalation chambers for 4 weeks to BD-diol to determine the mutagenic potency estimates for the same exposure levels and to compare these estimates to those reported for BD-exposed female mice and rats where comparable blood levels of BD-diol were achieved. Measurements of plasma levels of BD-diol (via GC/MS methodology) showed that (i) BD-diol accumulated in a sub-linear fashion during single 6-h exposures to >200 ppm BD; (ii) BD-diol accumulated in a linear fashion during single or repeated exposures to 6-18 ppm BD and then in a sub-linear fashion with increasing levels of BD-diol exposure; and (iii) exposures of mice and rats to 18 ppm BD-diol were equivalent to those produced by 200 ppm BD exposures (with exposures to 36 ppm BD-diol yielding plasma levels approximately 25% of those produced by 625 ppm BD exposures). Measurements of Hprt mutant frequencies (via the T cell cloning assay) showed that repeated exposures to 18 and 36 ppm BD-diol were significantly mutagenic in mice and rats. The resulting data indicated that BD-diol derived metabolites (especially, 1,2-dihydroxy-3,4-epoxybutane) have a narrow range of mutagenic effects confined to high-level BD (>or=200 ppm) exposures, and are responsible for nearly all of the mutagenic response in the rat and for a substantial portion of the mutagenic response in the mouse following high-level BD exposures.     

Persistence of 7-(2-hydroxyethyl) guanine-DNA adducts in rats exposed to ethene by inhalation

Quantification of 7 2 hydroxyethyl guanine 7 HEG adduct in DNA of livers and lymphocytes of male Sprague-Dawley rats exposed to 300 ppm ethene by inhalation 12 h a day for three consecutive days was performed to evaluate the potential of ethene to produce DNA adducts in these tissues. The persistence of 7 HEG in livers and lymphocytes was studied in rats sacrificed 0, 1, 5, and 20 days after the last exposure. DNA samples from control and treated animals were analysed for 7 HEG and 7 methylguanine 7 MG adducts by thin layer chromatography TLC combined with a high pressure liquid chromatography HPLC assay. After a 3 day exposure to ethene, 7 HEG accumulated to a similar extent in liver and lymphocytes, with the mean adduct level of 7.0 0.7 adducts per 107 nucleotides in liver and 7.4 0.7 adducts per 107 nucleotides in lymphocytes of rats sacrificed immediately after cessation of exposure. The approximate half life of 7 HEG was 5 days in liver and 3 days in lymphocytes, which is consistent with the loss of adduct primarily by spontaneous depurination. In addition, the background levels of 7 HEG and 7 MG were determined in the liver and lymphocytes from the control rats.