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James A Swenberg

Publications and source records attributed to James A Swenberg.

At least 19 recordsLinked to original sources

N-terminal globin adducts as biomarkers for formation of butadiene derived epoxides.

The aim of this review is to summarize our recent data on butadiene (BD) derived hemoglobin adducts as biomarkers for the internal formation of the individual epoxides formed by butadiene (BD). It is well known that BD is oxidized by cytochrome P450s to several epoxides that form DNA and protein adducts. 1,2-Epoxy-3-butene (EB), 1,2;3,4-diepoxybutane (DEB) and 1,2-epoxy-3,4-butanediol (EB-diol) form N-(2-hydroxy-3-butenyl)-valine (HB-Val), N,N-(2,3-dihydroxy-1,4-butadiyl)-valine (pyr-Val) and N-(2,3,4-trihydroxybutyl)-valine (THB-Val) adducts, respectively. The analysis of HB-Val and THB-Val by the modified Edman degradation and GC-MS/MS has generated valuable insights into BD metabolism across species. In addition, a recently established method for the analysis of pyr-Val has been proven to be suitable for detection of pyr-Val in rodents exposed to BD as low as 1 ppm. These technologies have been applied to study a wide range of exposures to BD, EB, DEB, and 3-butene-1,2-diol as a precursor of EB-diol in male and female mice and rats. Altogether the data have shown that BD metabolism is species and concentration dependent, consistent with metabolism and carcinogenesis data. Mice form much more HB-Val and pyr-Val than rats, especially at low exposures. After 10 days of inhalation exposure to 3 ppm BD, mice formed 12.5-fold more pyr-Val than rats. In contrast, the amounts of THB-Val were similar in mice and rats exposed to 3 or 62.5 ppm BD. Furthermore, it appears that the formation of THB-Val is supralinear in mice and rats due to saturation of metabolic activation pathways. Gender differences in metabolism are less well established. One study with male and female rats exposed to 1000 ppm BD for 90 days demonstrated a 1.6-, 3.5- and 2.0-fold gender difference in formation of HB-Val, pyr-Val and THB-Val, respectively, with females being more efficient in epoxide formation. The analyses of BD derived protein adducts correlate well with the observed species and gender differences in BD-carcinogenesis and suggest that DEB may indeed be the most important metabolite.

Animals↗

Molecular epidemiological studies in 1,3-butadiene exposed Czech workers: female-male comparisons.

Results of a recent molecular epidemiological study of 1,3-butadiene (BD) exposed Czech workers, conducted to compare female to male responses, have confirmed and extended the findings of a previously reported males only study (HEI Research Report 116, 2003). The initial study found that urine concentrations of the metabolites 1,2-dihydroxy-4-(acetyl) butane (M1) and 1-dihydroxy-2-(N-acetylcysteinyl)-3-butene (M2) and blood concentrations of the hemoglobin adducts N-[2-hydroxy-3-butenyl] valine (HB-Val) and N-[2,3,4-trihydroxy-butyl] valine (THB-Val) constitute excellent biomarkers of exposure, both being highly correlated with BD exposure levels, and that GST genotypes modulate at least one metabolic pathway, but that irreversible genotoxic effects such as chromosome aberrations and HPRT gene mutations are neither associated with BD exposure levels nor with worker genotypes (GST [glutathione-S-transferase]-M1, GSTT1, CYP2E1 (5' promoter), CYP2E1 (intron 6), EH [epoxide hydrolase] 113, EH139, ADH [alcohol dehydrogenase]2 and ADH3). The no observed adverse effect level (NOAEL) for chromosome aberrations and HPRT mutations was 1.794 mg/m(3) (0.812 ppm)--the mean exposure level for the highest exposed worker group in this initial study. The second Czech study, reported here, initiated in 2003, included 26 female control workers, 23 female BD exposed workers, 25 male control workers and 30 male BD exposed workers (some repeats from the first study). Multiple external exposure measurements (10 full 8-h shift measures by personal monitoring per worker) over a 4-month period before biological sample collections showed that BD workplace levels were lower than in the first study. Mean 8-h TWA exposure levels were 0.008 mg/m(3) (0.0035 ppm) and 0.397 mg/m(3) (0.180 ppm) for female controls and exposed, respectively, but with individual single 8-h TWA values up to 9.793 mg/m(3) (4.45 ppm) in the exposed group. Mean male 8-h TWA exposure levels were 0.007 mg/m(3) (0.0032 ppm) and 0.808 mg/m(3) (0.370 ppm) for controls and exposed, respectively; however, the individual single 8-h TWA values up to 12.583 mg/m(3) (5.72 ppm) in the exposed group. While the urine metabolite concentrations for both M1 and M2 were elevated in exposed compared to control females, the differences were not significant, possibly due to the relatively low BD exposure levels. For males, with greater BD exposures, the concentrations of both metabolites were significantly elevated in urine from exposed compared to control workers. As in the first study, urine metabolite excretion patterns in both sexes revealed conjugation to be the minor detoxification pathway (yielding the M2 metabolite) but both M1 and M2 concentration values were lower in males in this second study compared to their concentrations in the first, reflecting the lower external exposures of males in this second study compared to the first. Of note, females showed lower concentrations of both M1 and M2 metabolites in the urine per unit of BD exposure than did males while exhibiting the same M1/(M1+M2) ratio, reflecting the same relative utilization of the hydrolytic (producing M1) and the conjugation (producing M2) detoxification pathways as males. Assays for the N,N-(2,3-dihydroxy-1,4-butadyl) valine (pyr-Val) hemoglobin (Hb) adduct, which is specific for the highly genotoxic 1,2,3,4-diepoxybutane (DEB) metabolite of BD, have been conducted on blood samples from all participants in this second Czech study. Any adduct that may have been present was below the limits of quantitation (LOQ) for this assay for all samples, indicating that production of this important BD metabolite in humans is below levels produced in both mice and rats exposed to as little as 1.0 ppm BD by inhalation (J.A. Swenberg, M.G. Bird, R.J. Lewis, Future directions in butadiene risk assessment, Chem. Biol. Int. (2006), this issue). Results of assays for the HB-Val and THB-Val hemoglobin adducts are pending. HPRT mutations, determined by cloning assays, and multiple measures of chromosome level changes (sister-chromatid exchanges [SCE], aberrations determined by conventional methods and FISH) again showed no associations with BD exposures, confirming the findings of the initial study that these irreversible genotoxic changes do not arise in humans occupationally exposed to low levels of BD. Except for lower production of both urine metabolites in females, no female-male differences in response to BD exposures were detected in this study. As in the initial study, there were no significant genotype associations with the irreversible genotoxic endpoints. However, as in the first, differences in the metabolic detoxification of BD as reflected in relative amounts of the M1 and M2 urinary metabolites were associated with genotypes, this time both GST and EH.

Acetylcysteine↗

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.

Aging↗

Quantitative analysis of N-terminal valine peptide adducts specific for 1,2-epoxy-3-butene.

Butadiene (BD) metabolism shows gender, species and concentration dependency, making the extrapolation of animal results to humans complex. BD is metabolized mainly by cytochrome P450 2E1 to three epoxides, 1,2-epoxy-3-butene (EB), 1,2;3,4-diepoxybutane (DEB) and 1,2-epoxy-butanediol (EB-diol). For accurate risk assessment it is important to elucidate species differences in the internal formation of the individual epoxides in order to assign the relative risks associated with their different mutagenic potencies. Analysis of N-terminal globin adducts is a common approach for monitoring the internal formation of BD derived epoxides. Our long term strategy is to develop an LC-MS/MS method for simultaneous detection of all three BD hemoglobin adducts. This approach is modeled after the recently reported immunoaffinity LC-MS/MS method for the cyclic N,N-(2,3-dihydroxy-1,4-butadyil)-valine (pyr-Val, derived from DEB). We report herein the analysis of the EB-derived 2-hydroxyl-3-butenyl-valine peptide (HB-Val). The procedure utilizes trypsin hydrolysis of globin and immunoaffinity (IA) purification of alkylated heptapeptides. Quantitation is based on LC-MS/MS monitoring of the transition from the singly charged molecular ion of HB-Val (1-7) to the a(1) fragment. Human HB-Val (1-11) was synthesized and used for antibody production. As internal standard, the labeled rat-[(13)C(5)(15)N]-Val (1-11) was prepared through direct alkylation of the corresponding peptide with EB. Standards were characterized and quantified by LC-MS/MS and LC-UV. The method was validated with different amounts of human HB-Val standard. The recovery was >75% and coefficient of variation <25%. The LOQ was set to 100 fmol/injection. For a proof of principal experiment, globin samples from male and female rats exposed to 1000 ppm BD for 90 days were analyzed. The amounts of HB-Val present were 268.2+/-56 and 350+/-70 pmol/g (mean+/-S.D.) for males and females, respectively. No HB-Val was detected in controls. These data are much lower compared to previously reported values measured by GC-MS/MS. The difference may be due higher specificity of the LC-MS/MS method to the N-terminal peptide from the alpha-chain versus derivatization of both alpha- and beta-chain by Edman degradation, and possible instability of HB-Val adducts during long term storage (about 10 years) between the analyses. These differences will be resolved by examining recently collected samples, using the same internal standard for parallel analysis by GC-MS/MS and LC-MS/MS. Based on our experience with pyr-Val adduct assay we anticipate that this assay will be suitable for evaluation of HB-Val in multiple species.

Animals↗

Phenotypic anchoring of acetaminophen-induced oxidative stress with gene expression profiles in rat liver.

Toxicogenomics provides the ability to examine in greater detail the underlying molecular events that precede and accompany toxicity, thus allowing prediction of adverse events at much earlier times compared to classical toxicological end points. Acetaminophen (APAP) is a pharmaceutical that has similar metabolic and toxic responses in rodents and humans. Recent gene expression profiling studies with APAP found an oxidative stress signature at a subtoxic dose that we hypothesized can be phenotypically anchored to conventional biomarkers of oxidative stress. Liver tissue was obtained from experimental animals used to generate microarray data, where male rats were given APAP at subtoxic (150 mg/kg) or overtly toxic (1500 and 2000 mg/kg) doses and sacrificed at 6, 24, or 48 h. Oxidative stress in liver was evaluated by a diverse panel of markers that included assessing expression of base excision repair (BER) genes, quantifying oxidative lesions in genomic DNA, and evaluating protein and lipid oxidation. A subtoxic dose of APAP produced significant accumulation of nitrotyrosine protein adducts. Both subtoxic and toxic doses caused a significant increase in 8-hydroxy-deoxyguanosine (8-OH-dG) as well as a significant decrease in glutathione (GSH) content. Only toxic doses of APAP significantly induced expression levels of BER genes. None of the doses examined resulted in a significant increase in the number of abasic sites or in the amount of lipid peroxidation. The accumulation of nitrotyrosine and 8-OH-dG adducts along with reduced GSH content in the liver phenotypically anchors the oxidative stress gene expression signature observed with a subtoxic dose of APAP, lending support to the validity of gene expression studies as a sensitive and biologically meaningful end point in toxicology.

Acetaminophen↗

XRCC1 genotype and breast cancer: functional studies and epidemiologic data show interactions between XRCC1 codon 280 His and smoking.

Tobacco smoke produces oxidative and alkylative DNA damage that necessitates repair by base excision repair coordinated by X-ray cross-complementing gene 1 (XRCC1). We investigated whether polymorphisms in XRCC1 alter DNA repair capacity and modify breast cancer risk associated with smoking. To show the functionality of the 280His variant, we evaluated single-strand break (SSB) repair capacity of isogenic Chinese hamster ovary cells expressing human forms of XRCC1 after exposure to hydrogen peroxide (H(2)O(2)), methyl methanesulfonate (MMS), or camptothecin by monitoring NAD(P)H. We used data from the Carolina Breast Cancer Study (CBCS), a population-based, case-control study that included 2,077 cases (786 African Americans and 1,281 Whites) and 1,818 controls (681 African Americans and 1,137 Whites), to examine associations among XRCC1 codon 194, 280, and 399 genotypes, breast cancer, and smoking. Odds ratios and 95% confidence intervals (95% CI) were calculated by unconditional logistic regression. Only cells expressing the 280His protein accumulated SSB, indicated by NAD(P)H depletion, from both H(2)O(2) and MMS exposures. In the CBCS, positive associations were observed between breast cancer and smoking dose for participants with XRCC1 codon 194 Arg/Arg (P(trend) = 0.046), 399 Arg/Arg (P(trend) = 0.012), and 280 His/His or His/Arg (P(trend) = 0.047) genotypes. The 280His allele was in strong linkage disequilibrium with 194Arg (Lewontin's D' = 1.0) and 399Arg (D' = 1.0). These data suggest that less common, functional polymorphisms may lie within common haplotypes and drive gene-environment interactions.

Aged↗

Profiling of ecdysteroids in complex biological samples using liquid chromatography/ion trap mass spectrometry.

A sensitive method using high-performance liquid chromatography coupled to a mass spectrometer with electrospray ionization source (HPLC/ESI-MS) was developed for detection of ecdysteroids in biological samples. We report here for the first time that ecdysteroids can be classified into three groups based on ESI full-scan mass spectra: group 1 (ecdysone (E), 2-deoxyecdysone (2dE), 2,22-dideoxyecdysone (3beta5beta-KT), and 3alpha5alpha[H]-dihydroxycholest-7-en-6-one (3alpha5alpha-KD)), in which loss of one molecule of water from the protonated molecular ion ([M+H](+)) represents the dominant ion; group 2 (20-hydroxyecdysone (20E), makisterone A (MakA), 3beta5beta-KD, and 3beta5alpha-KD), in which [M+H](+) is a major ion but some water loss is observed; and group 3 (muristerone A (MurA) and ponasterone A (PonA)), in which [M+H](+) is the dominant ion with no water loss observed. Based on the analytical procedure in combination with structural information from the group classification and with the application of source-induced dissociation, we identified free ecdysteroids in biological samples: 20,26-dihydroxyecdysone and ecdysonic acid in the larval hemolymph, and the progressive metabolism of 26-hydroxyecdysone (26E) to 3alpha-26E from day-1 to day-3 embryos of the tobacco hornworm Manduca sexta.

Animals↗

LC/MS/MS method for the quantitation of trans-2-hexenal-derived exocyclic 1,N(2)-propanodeoxyguanosine in DNA.

trans-2-Hexenal is an alpha,beta-unsaturated aldehyde to which humans are exposed daily in small amounts. Hexenal has demonstrated mutagenicity and genotoxicity in vitro and reacts with deoxyguanosine to form diastereomeric hexenal-derived exocyclic 1,N(2)-propanodeoxyguanosine (Hex-PdG) adducts. A highly sensitive and specific method for the measurement of Hex-PdG in DNA has not previously been available. An LC/MS/MS assay for the quantitation of Hex-PdG, using [(13)C4(15)N2]Hex-PdG as an internal standard, was developed, to assess binding of hexenal to DNA. Samples were purified prior to analysis by centrifuge filtration and solid phase extraction and analyzed by LC/MS/MS in the selected reaction monitoring (SRM) mode (SRM m/z 366.2 --> 250.2 for Hex-PdG; SRM m/z 372.2 --> 256.2 for [(13)C4(15)N2]Hex-PdG). Recovery of standards was 89% or greater, and quantitation was unaffected by the addition of increasing concentrations of calf thymus DNA (ctDNA). The limit of quantitation, determined in samples of 200 microg of ctDNA spiked with analyte standard, was 0.015 fmol/microg DNA, which corresponds to approximately 5 Hex-PdG/10(9) unmodified nucleotides. Hex-PdG was detected in ctDNA treated with 0.021 microM, 0.21 microM, or 2.1 mM hexenal but not in untreated DNA. Furthermore, Hex-PdG was not detected in DNA exposed to reactive oxygen species-mediated deoxyribose attack and lipid peroxidation, which resulted in a significant increase in the malondialdehyde-derived pyrimido[1,2-a]purin-10(3H)one. Hex-PdG was not detected in DNA of untreated rat liver, but Hex-PdG in hexenal-treated calf thymus DNA was quantifiable when spiked into the rat liver DNA at 0.035 or 0.35 fmol/microg DNA. These data indicate that Hex-PdG is formed following hexenal treatment and that this method is suitable for in vitro or in vivo assessment of Hex-PdG formation.

Aldehydes↗

Epifluorescence microscopy and image analysis of high-level polycyclic aromatic hydrocarbon contamination in soils.

Interactions between polycyclic aromatic hydrocarbons (PAHs) and soil are an important determinant of their chemical availability and transport. Laboratory examination of microscale PAH-soil interaction is limited by the availability of methods for particle-scale observation. Inverted epifluorescence microscopy, combined with digital photography and computer image analysis, was evaluated for specificity and linearity using dissolved PAHs. A pyrene filter (excitation wavelength, 360-400 nm; emission wavelength, 450-520 nm) gave nonspecific PAH fluorescence, and bias for fluoranthene, benzo[b]fluoranthene, benzo[g,h,i]perylene, and benz[a]anthracene was quantified in comparison to that for pyrene. Concentrations ranging from 1 to 10 mM for anthracene, fluoranthene, and pyrene and from 1 to 50 mM for naphthalene produced a linear response with low interpixel variability. Liquid-phase analyses validated use of the technique for the descriptive analysis of PAH distribution in solid samples, but liquid-phase calibration was not quantitative for spiked or field-contaminated soils. The mean luminance for three field soils was proportional to the values predicted from their chemically measured concentrations and to values from spiked, aged, uncontaminated materials. Image analysis of laboratory- and field-contaminated samples determined the area distribution of fluorescent intensity and the size of fluorescent areas exceeding a threshold luminance. These qualitative descriptions of the microscale spatial distribution of PAH contamination are presented as potential endpoints for future research on biogeochemical interactions in heavily contaminated solids.

Hydrogen-Ion Concentration↗

Pyrimido[1,2-a]-purin-10(3H)-one, M1G, is less prone to artifact than base oxidation.

Pyrimido[1,2-a]-purin-10(3H)-one (M1G) is a secondary DNA damage product arising from primary reactive oxygen species (ROS) damage to membrane lipids or deoxyribose. The present study investigated conditions that might lead to artifactual formation or loss of M1G during DNA isolation. The addition of antioxidants, DNA isolation at low temperature or non-phenol extraction methods had no statistically significant effect on the number of M1G adducts measured in either control or positive control tissue samples. The number of M1G adducts in nuclear DNA isolated from brain, liver, kidney, pancreas, lung and heart of control male rats were 0.8, 1.1, 1.1, 1.1, 1.8 and 4.2 M1G/10(8) nt, respectively. In rat liver tissue, the mitochondrial DNA contained a 2-fold greater number of M1G adducts compared with nuclear DNA. Overall, the results from this study demonstrated that measuring M1G is a reliable way to assess oxidative DNA damage because the number of M1G adducts is significantly affected by the amount of ROS production, but not by DNA isolation procedures. In addition, this study confirmed that the background number of M1G adducts reported in genomic DNA could have been overestimated by one to three orders of magnitude in previous reports.

Animals↗

Formation of M1G-dR from endogenous and exogenous ROS-inducing chemicals.

The present study provides fundamental information regarding the production of M1G-dR by ROS. To investigate the production of M1G-dR from deoxyribose damage as caused by ROS, calf thymus DNA (CT-DNA) was incubated with NAD(P)H, CuCl2, and various concentrations of hydrogen peroxide (H2O2). The incubation of CT-DNA with H2O2 resulted in concentration-dependent increases in the number of M1G-dR adducts. In subsequent experiments, 1,4-tetrachlorobenzoquinone or catechol estrogens were evaluated for their effects on M1G-dR formation. In addition, the role of lipid peroxidation in the formation of M1G-dR was verified using an in vitro lipid peroxidation model which consisted of methyl esters of either fish oil or purified fatty acids found in cellular membranes. This experiment confirmed that M1G-dR is a major DNA adduct produced by lipid peroxidation. Furthermore, the number of double bonds in polyunsaturated fatty acids was found to be the key factor in the formation of M1G-dR. The findings obtained from this study provide important information regarding the molecular pathways for M1G-dR formation by ROS, which is an essential element in understanding and evaluating the genotoxicity of a variety of ROS-inducing chemicals.

DNA↗

Effects of ethylene oxide and ethylene inhalation on DNA adducts, apurinic/apyrimidinic sites and expression of base excision DNA repair genes in rat brain, spleen, and liver.

Ethylene oxide (EO) is an important industrial chemical that is classified as a known human carcinogen (IARC, Group 1). It is also a metabolite of ethylene (ET), a compound that is ubiquitous in the environment and is the most used petrochemical. ET has not produced evidence of cancer in laboratory animals and is "not classifiable as to its carcinogenicity to humans" (IARC, Group 3). The mechanism of carcinogenicity of EO is not well characterized, but is thought to involve the formation of DNA adducts. EO is mutagenic in a variety of in vitro and in vivo systems, whereas ET is not. Apurinic/apyrimidinic sites (AP) that result from chemical or glycosylase-mediated depurination of EO-induced DNA adducts could be an additional mechanism leading to mutations and chromosomal aberrations. This study tested the hypothesis that EO exposure results in the accumulation of AP sites and induces changes in expression of genes for base excision DNA repair (BER). Male Fisher 344 rats were exposed to EO (100 ppm) or ET (40 or 3000 ppm) by inhalation for 1, 3 or 20 days (6h/day, 5 days a week). Animals were sacrificed 2h after exposure for 1, 3 or 20 days as well as 6, 24 and 72 h after a single-day exposure. Experiments were performed with tissues from brain and spleen, target sites for EO-induced carcinogenesis, and liver, a non-target organ. Exposure to EO resulted in time-dependent increases in N7-(2-hydroxyethyl)guanine (7-HEG) in brain, spleen, and liver and N7-(2-hydroxyethyl)valine (7-HEVal) in globin. Ethylene exposure also induced 7-HEG and 7-HEVal, but the numbers of adducts were much lower. No increase in the number of aldehydic DNA lesions, an indicator of AP sites, was detected in any of the tissues between controls and EO-, or ET-exposed animals, regardless of the duration or strength of exposure. EO exposure led to a 3-7-fold decrease in expression of 3-methyladenine-DNA glycosylase (Mpg) in brain and spleen in rats exposed to EO for 1 day. Expression of 8-oxoguanine DNA glycosylase, Mpg, AP endonuclease (Ape), polymerase beta (Pol beta) and alkylguanine methyltransferase were increased by 20-100% in livers of rats exposed to EO for 20 days. The only effects of ET on BER gene expression were observed in brain, where Ape and Pol beta expression were increased by less than 20% after 20 days of exposure to 3000 ppm. These data suggest that DNA damage induced by exposure to EO is repaired without accumulation of AP sites and is associated with biologically insignificant changes in BER gene expression in target organs. We conclude that accumulation of AP sites is not a likely primary mechanism for mutagenicity and carcinogenicity of EO.

Administration, Inhalation↗

Anti-AIDS agents 65: investigation of the in vitro oxidative metabolism of 3',4'-Di-O-(-)-camphanoyl-(+)-cis-khellactone derivatives as potent anti-hiv agents.

3',4'-Di-O-(-)-camphanoyl-(+)-cis-khellactone (DCK) is a synthetic khellactone ester that exhibits potent in vitro anti-human immunodeficiency virus (HIV) activity with a mechanism distinct from clinically used anti-HIV agents. Several series of mono- and di-substituted DCK derivatives (DCKs) have previously been synthesized, and their structure-activity relationships are well established. To optimize DCK as a drug lead and to guide further structural modifications, metabolic stabilities and metabolite structures were analyzed. In vitro metabolic stabilities of DCKs in human liver microsomes were assessed using high performance liquid chromatography (HPLC) with UV detection to establish structure-metabolism relationships (SMRs). HPLC coupled with ion trap mass spectrometry was used to identify the metabolite structures. The results indicated that DCKs undergo rapid oxidation on the lipophilic camphanoyl moieties and the substituents on the khellactone do not alter the rate or the metabolic pathways for this compound type. Our SMR and metabolite analysis study suggested that the two camphanoyl ester moieties are the determinants of the low metabolic stability and that structural alteration in the two esters may be necessary to improve metabolic profiles of DCKs.

Anti-HIV Agents↗

Standardizing global gene expression analysis between laboratories and across platforms.

To facilitate collaborative research efforts between multi-investigator teams using DNA microarrays, we identified sources of error and data variability between laboratories and across microarray platforms, and methods to accommodate this variability. RNA expression data were generated in seven laboratories, which compared two standard RNA samples using 12 microarray platforms. At least two standard microarray types (one spotted, one commercial) were used by all laboratories. Reproducibility for most platforms within any laboratory was typically good, but reproducibility between platforms and across laboratories was generally poor. Reproducibility between laboratories increased markedly when standardized protocols were implemented for RNA labeling, hybridization, microarray processing, data acquisition and data normalization. Reproducibility was highest when analysis was based on biological themes defined by enriched Gene Ontology (GO) categories. These findings indicate that microarray results can be comparable across multiple laboratories, especially when a common platform and set of procedures are used.

Gene Expression Profiling↗

Oxidative DNA damage from potassium bromate exposure in Long-Evans rats is not enhanced by a mixture of drinking water disinfection by-products.

Public drinking water treated with chemical disinfectants contains a complex mixture of disinfection by-products (DBPs) for which the relative toxicity of the mixtures needs to be characterized to accurately assess risk. Potassium bromate (KBrO(3)) is a by-product from ozonation of high-bromide surface water for production of drinking water and is a rodent carcinogen that produces thyroid, mesothelial, and renal tumors. The proposed mechanism of KBrO(3) renal carcinogenesis involves the formation of 8-oxoguanine (8-oxoG), a promutagenic base lesion in DNA typically removed through base excision repair (BER). In this study, male Long-Evans rats were exposed via drinking water to carcinogenic concentrations of KBrO(3) (0.4 g/L), 3-chloro-4-(dichloromethyl)-5-hydroxy-2(5H)-furanone (0.07 g/L), chloroform (1.8 g/L), bromodichloromethane (0.7 g/L), or a mixture of all these chemicals at the same concentrations for 3 weeks. Half of one kidney was processed for microscopic examination, and the remaining kidney was frozen for isolation of genomic DNA. Levels of 8-oxoG were measured using HPLC with electrochemical detection in DNA samples incubated with formamidopyrimidine-DNA glycosylase. Aldehydic lesions (e.g. abasic sites) in DNA samples were quantitated using an aldehyde-reactive probe slot-blot assay. Treatment with KBrO(3) produced a measurable increase of 8-oxoG in the kidney, and this effect was greater than that produced by treatment with the DBP mixture. No other single chemical treatment caused measurable increases of 8-oxoG. The mixture effect on the amount of 8-oxoG observed in this study suggests an interaction between chemicals that reduced the generation of oxidative DNA damage. No increases in abasic sites were observed with treatment, but a decrease was apparent in the rats treated with the DBP mixture. These data are consistent with previous studies where chronic exposure to this chemical mixture in drinking water resulted in a less than additive carcinogenic response in Tsc2 mutant Long-Evans rats.

Animals↗

Expression of base excision DNA repair genes as a biomarker of oxidative DNA damage.

Oxidative stress induced DNA damage is considered to be the most common insult affecting the genome. Moreover, it is recognized as a common pathway to mutations and is suggested to play a major role in the development of chronic diseases such as cancer. However, current analytical methods used to detect oxidative DNA damage have been hampered by both technical and biological obstacles. These include spurious oxidation during DNA isolation and processing, and the inherent removal of damaged bases by numerous operating DNA repair systems. The removal of oxidized bases is performed predominantly by the base excision repair (BER) pathway and it has been shown that induction of DNA repair genes occurs in response to oxidative stress. Here, we demonstrate the utility of measuring changes in expression of BER genes as a sensitive in vivo biomarker for oxidative DNA damage.

Biomarkers↗

Analysis of 7-methylguanine using isotope dilution and gas chromatography/electron-capture negative chemical ionization mass spectrometry.

This paper presents results obtained for in vivo endogenous and exogenous 7-methylguanine (7-MG) analyzed using a method incorporating gas chromatography with electron-capture negative chemical ionization mass spectrometry and isotope dilution (GC/EC-ID-MS). 13C4-Labeled 7-MG was synthesized to serve as an internal standard to improve accuracy of quantitation, and was used to analyze 7-MG in livers of control mice and dacarbazine-treated mice. The results confirm that 7-MG in tissue DNA can be measured using this GC/EC-ID-MS method with excellent sensitivity and specificity. Administration of 0, 30, and 60 mg/kg dacarbazine to mice led to dose-dependent increases in the formation of 7-MG. The results indicate that this method could be applied to the analysis of endogenous and exogenous 7-MG in human tissues for future molecular epidemiology studies on potential health effects caused by methylating agents.

Animals↗

Induction of cytotoxicity, aldehydic DNA lesions, and poly(ADP-ribose) polymerase-1 activation by catechol derivatives of pentachlorophenol in calf thymus DNA and in human breast cancer cells.

The purpose of this study was to investigate the degree of chlorination of catechol (CAT) derivatives of pentachlorophenol (PCP) on the induction of cytotoxicity and DNA damaging effects in calf thymus DNA (ct-DNA) and in two human breast carcinoma cell lines. Results indicated that with the addition of the transition metal copper(II), increases in the amount of aldehydic DNA lesions (ADL) were detected in ct-DNA exposed to PCP-derived CATs over the corresponding control. The DNA lesions induced by various degrees of chlorination of PCP-derived CATs decrease in the rank order CAT congruent with 4-chlorocatechol (4-ClCAT) > 4,5-dichlorocatechol (4,5-Cl2CAT) > 3,4,5-trichlorocatechol (3,4,5-Cl3CAT) > tetrachlorocatechol (Cl4CAT). In contrast, Cl4CAT was the only congeneric form of PCP-derived catechols that induced a significant increase in the number of ADL in human MCF-7 cells, and this only occurred when glutathione was depleted. Pretreatment with copper(I) and iron(II) chelators significantly reduced the formation of ADL in cells exposed to Cl4CAT. The data also indicated that the ADL induced by Cl4CAT in MCF-7 cells contain approximately 70% putrescine excisable ADL. This evidence confirmed that the ADL induced by Cl4CAT in MCF-7 cells were derived from oxidative events. In addition, we demonstrated that the depletion of NAD(P)H in human T47D cells exposed to chlorinated CATs decreased in the rank order Cl4CAT >> 4-ClCAT congruent with CAT. The depletion of NAD(P)H induced by Cl4CAT in T47D cells was partially blocked by catalase, superoxide dismutase, dimethyl sulfoxide, and copper(I) and iron(II) specific chelators. Additionally, the depletion of NAD(P)H in T47D cells exposed to Cl4CAT (1-10 microM) was completely blocked by three types of poly(ADP-ribose) polymerase-1 inhibitors. This evidence suggests that Cl4CAT induces an imbalance in DNA repair and the subsequent accumulation of DNA strand breaks in human cultured cells. Overall, these findings indicate that dechlorination may decrease the potentials of chlorinated catechols to induce oxidative DNA lesions and cytotoxic effects in living cells.

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