Investigation of the cumulative tissue doses of naphthoquinones in human serum using protein adducts as biomarker of exposure

Both 1,2-naphthoquinone (1,2-NPQ) and 1,4-naphthoquinone (1,4-NPQ) are reactive metabolites of naphthalene that are thought to be responsible for the naphthalene-induced cytotoxicity and genotoxicity. The aim of this study was to investigate the cumulative tissue dose of 1,2-NPQ and 1,4-NPQ in human serum derived from blood donors in Taiwan via measurements of albumin adducts by a methodology, which employs trifluoroacetic acid anhydride and methanesulfonic acid to selectively cleave cysteinyl adducts on proteins. Both 1,2-NPQ and 1,4-NPQ adducts were detected in all male and female subjects (n = 22). The median levels of 1,2-NPQ adduct in human subjects were estimated to be 268 (range 139-857) and 203 (range 128-1352) (pmol/g) in male (n = 11) and female (n = 11) subjects, respectively. In contrast, the median levels of 1,4-NPQ adduct were estimated to be 45.0 (range 22.0-117) and 38.9 (range 21.5-172) (pmol/g) in male and female subjects, respectively. We noticed that levels of 1,2-NPQ adduct were significantly correlated with those of 1,4-NPQ adduct (correlation coefficient r = 0.643, p < 0.01). Results from in vitro experiments confirmed that the production of naphthoquinones-derived adducts on serum albumin increased with increased concentration of naphthoquinones (0-100 μM). Linear relationships were observed over the range of concentration. Time-course experiments suggested that both 1,2-NPQ and 1,4-NPQ-derived adducts rapidly reached maximum values at 10 min mark and remained constant thereafter. The reaction rate constant analyses indicated that the second-order rate constants, representing in vitro reactions between naphthoquinones and cysteine residues of serum albumin, were estimated to be 0.0044/0.0002 L(g protein)⁻¹ h⁻¹, respectively. Overall, the cumulative tissue doses of 1,4-NPQ (217-316 nM h) in male and female subjects were ∼3-fold greater than those of 1,2-NPQ (76-98 nM h) in the study population. The initial concentrations of serum 1,2-NPQ and 1,4-NPQ in the study population were estimated to be between 145-188 and 807-1175 nM, respectively. We conclude that the relatively large amounts of naphthoquinones present in human serum may point to toxicological consequences.     

Depurinating naphthalene–DNA adducts in mouse skin related to cancer initiation

Naphthalene has been shown to be a weak carcinogen in rats. To investigate its mechanism of metabolic activation and cancer initiation, mice were topically treated with naphthalene or one of its metabolites, 1-naphthol, 1,2-dihydrodiolnaphthalene (1,2-DDN), 1,2-dihydroxynaphthalene (1,2-DHN), and 1,2-naphthoquinone (1,2-NQ). After 4 h, the mice were sacrificed, the treated skin was excised, and the depurinating and stable DNA adducts were analyzed. The depurinating adducts were identified and quantified by ultraperformance liquid chromatography/tandem mass spectrometry, whereas the stable adducts were quantified by ³²P-postlabeling. For comparison, the stable adducts formed when a mixture of the four deoxyribonucleoside monophosphates was treated with 1,2-NQ or enzyme-activated naphthalene were also analyzed. The depurinating adducts 1,2-DHN-1-N3Ade and 1,2-DHN-1-N7Gua arise from reaction of 1,2-NQ with DNA. Similarly, the major stable adducts appear to derive from the 1,2-NQ. The depurinating DNA adducts are, in general, the most abundant. Therefore, naphthalene undergoes metabolic activation to the electrophilic ortho-quinone, 1,2-NQ, which reacts with DNA to form depurinating adducts. This is the same mechanism as other weak carcinogens, such as the natural and synthetic estrogens, and benzene.     

A VANADIUM BROMOPEROXIDASE CATALYZES THE FORMATION OF HIGH‐MOLECULAR‐WEIGHT COMPLEXES BETWEEN BROWN ALGAL PHENOLIC SUBSTANCES AND ALGINATES1

The interaction between phenolic substances (PS) and alginates (ALG) has been suggested to play a role in the structure of the cell walls of brown seaweeds. However, no clear evidence for this interaction was reported. Vanadium bromoperoxidase (VBPO) has been proposed as a possible catalyst for the binding of PS to ALG. In this work, we studied the interaction between PS and ALG from brown algae using size exclusion chromatography (SEC) and optical tweezers microscopy. The analysis by SEC revealed that ALG forms a high‐molecular‐weight complex with PS. To study the formation of this molecular complex, we investigated the in vitro interaction of purified ALG from Fucus vesiculosus L. with purified PS from Padina gymnospora (Kütz.) Sond., in the presence or absence of VBPO. The interaction between PS and ALG only occurred when VBPO was added, indicating that the enzyme is essential for the binding process. The interaction of these molecules led to a reduction in ALG viscosity. We propose that VBPO promotes the binding of PS molecules to the ALG uronic acids residues, and we also suggest that PS are components of the brown algal cell walls.     

A pyridine adduct of bis(di-iso-butyldithiocarbamato-S,S′)cadmium(II): Multinuclear (C, N, Cd) CP/MAS NMR spectroscopy, crystal and molecular structure, and thermal behaviour

Crystalline bis(N,N-di-iso-butyldithiocarbamato-S,S′)(pyridine)cadmium(II) - adduct 1 was prepared and studied by means of multinuclear ¹³C, ¹⁵N, ¹¹³Cd CP/MAS NMR spectroscopy, single-crystal X-ray diffraction and simultaneous thermal analysis (STA). In molecular structure 1, the cadmium atom coordinates with four sulphur atoms and one nitrogen atom of pyridine, forming a coordination polyhedron [CdS₄N], whose geometry is an almost ideal tetragonal pyramidal (C_4v). The coordinated py molecule is in the apical position, while two structurally non-equivalent di-iso-butyldithiocarbamate ligands, playing the same terminal S,S′-chelating function, define the basal plane. To characterise additionally the structural state of the cadmium atom in this fivefold coordination, ¹¹³Cd chemical shift anisotropy (CSA) parameters, δ_aniso and η, were calculated from experimental MAS NMR spectra that revealed an almost axially symmetric ¹¹³Cd chemical shift tensor. From a combination of TG and DSC measurements taken under an argon atmosphere, we found that the mass of adduct 1 is lost in two steps involving initial desorption of coordinated py molecules with subsequent thermal destruction of liberated cadmium(II) di-iso-butyldithiocarbamate, with yellow-orange, fine-powdered solid CdS as the final product.     

Sequence-dependent formation of alkyl DNA adducts: A review of methods, results, and biological correlates

Understanding the influence of the DNA sequence on chemical-DNA interactions may provide insight into the processes of chemical carcinogenesis and mutagenesis. This article provides a brief overview of studies and methods devoted to examining the distribution of DNA adducts produced by alkylating agents. Particular emphasis is placed on discussion of DNA adducts generated by simple alkylating agents and the role that their distribution may play in the generation of mutational hotspots.     

Induction of abasic sites by the drinking-water mutagen MX in Salmonella TA100

Mutagen X (MX) is a chlorinated furanone that accounts for more of the mutagenic activity of drinking water than any other disinfection by-product. It is one of the most potent base-substitution mutagens in the Salmonella (Ames) mutagenicity assay, producing primarily GC to TA mutations in TA100. MX does not produce stable DNA adducts in cellular or acellular DNA. However, theoretical calculations predict that it might induce abasic sites, which it does in supercoiled plasmid DNA but not in rodents. To investigate the ability of MX to induce abasic sites in cellular DNA, we used an aldehydic site assay to detect abasic sites in DNA from Salmonella TA100 cells treated for 1.5 h with MX. At 0, 2.3, and 4.6 μM, MX induced mutant frequencies (revertants/10⁶ survivors) and percent survivals of 2 (100%), 14.9 (111%), and 59.3 (45%), respectively. The frequencies of abasic sites (sites/10⁵ nucleotides) for the control and two concentrations were 5.9, 6.2, and 9.7, respectively, with the frequency at the highest concentration being significant (P < 0.001). These results provide some evidence for the ability of MX to induce abasic sites in cellular DNA. However, the lack of a dose response makes it unclear whether this DNA damage underlies the mutagenic activity of MX.     

Adventitious root formation 'in vitro' in apple rootstocks (Malus pumila) II. Uptake and distribution of indol-3yl-acetic acid during the auxin-sensitive phase in M.9 and M.26

During the auxin-sensitive phase of root initiation, rates of 3-indolyl- [2-¹⁴C] acetic acid (IAA) uptake into the 1 cm bases of shoots of the apple rootstock M.9 ( Malus pumila Mill.) 'in vitro' were not significantly affected by the presence of 10⁻³ M phloroglucinol (PG) using either liquid or agar-solidified media. The use of a liquid medium did however reduce rates of uptake over a 10-day period of auxin application. The distribution of labelled IAA between the 1-cm base and the shoot remainder was not affected by PG.
Exposure of shoots of the difficult-to-root M.9 and the easy-to-root M.26, to 2.8 × 10⁻⁵ M IAA containing [2-¹⁴C] IAA revealed no positive correlation between the amount of label taken up by the 1-cm base and rooting performance. M.9 bases absorbed almost twice as much label as M.26 after 9 days but had produced only one-third as many roots. Measurements of label distribution between the 1-cm base and the shoot remainder showed that less than 10% of the label moved to the shoot remainder over a 6-day period of auxin application. Dose-response curves of IAA and rooting over the range 1 × 10⁻⁵ M and 3 × 10⁻³ M showed that root number in M.9 was at an optimum at 1 × 10⁻³ M IAA after 6 days whilst M.26 required only 1 × 10⁻⁴ M for a similar response. These data support the hypothesis that differences in rooting of the two rootstocks reflect differences in the endogenous metabolism of exogenous IAA and not differences in its rates of uptake or distribution in the shoots.     

Rational approaches to control of iron deficiency other than plant breeding and choice of resistant cultivars

Satisfactory progress has been made in recent years in preventing and correcting Fe deficiency in plants, and more can be expected in the future. Important advances include uses of acid- and Fe-fortified organic wastes and use of amended sulfur-pyrite mixes in soil. Three different approaches with organics are as an acidified matrix with Fe, as a means of chelating Fe, and as a carrier of acidifiers. Several procedures can help minimize Fe deficiency. (1) Avoid mis-management of soil physical properties and overirrigation. (2) Avoid nutrient imbalance, such as excess P or excess micronutrients. (3) Use preplant application of mildly acid-organic matter-Fe-sulfur or pyrite mixes worked into zones of soil or banded into seed rows. It is important that small bands or spots in soil be completely neutralized of CaCO₃. (4) Where foliar sprays can or need be used, especially to correct mild chlorosis, use ferrous compounds prepared to be delivered at pH 3± so that the Fe does not easily oxidize or precipitate in the solution. (5) For established trees that have become Fe deficient, inject, via slant drilling of small holes in tree trunks, dilute ferric ammonium citrate sufficient to supply not more than 100 mg kg^-1 Fe to leaves (dry weight basis). Most but not all species will respond. Procedure may be repeated in two or three weeks if necessary. (6) Iron chelates may be used in drip irrigation. If soil is sandy, soil pH not over 7.2, FeDTPA may be used; otherwise, FeEDDHA should be used. If the Fe is supplied with no other nutrients, pH may be at 4 and some FeSO₄ included to recycle the chelating agents. If Fe is used without chelating agents, the pH may be 1.0 or less and other nutrients included. (7) Urea-acid sulfate-Fe sulfate may be irrigated into soil around plants, especially if soil was polymer treated. (8) Efficiency of use of Fe chelates may be increased by making them slow release or by applying with seeds.     

Monitoring human exposure to carcinogens by DNA adduct measurement

Sensitive immunologic techniques are now available for the detection and quantitation of carcinogen-DNA adducts. We have developed a number of specific monoclonal antibodies which recognize DNA modified by particular carcinogens, including benzo[a]-py-rene, aminopyrene, 8-methoxypsoralen plus UVA light and vinyl chloride. These antibodies can be used in competitive enzyme-linked immunosorbent assays to quantitate adducts in DNA isolated from biological samples. Samples from treated animals as well as from humans with occupational or environmental exposure to carcinogens have been studied. In addition, antibodies can be used in indirect immunohistochemical studies to localize adduct formation in various tissues or cell types.Abbreviations BPDE-1 7,8-dihydroxy-9,10-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene - CTCL Cutaneous T cell lymphoma - ELISA enzyme linked immunosorbent assay - 8-MOP 8-methoxypsoralen - PUVA 8-MOP plus UVA irradiation     

Ecogenotoxicology in earthworms： A review

Pollutant dynamics and bioavailability greatly differ in soil and aquatic systems. Therefore, specific approaches and models are needed to assess the impact of soil contamination to terrestrial ecosystems. Earthworms among other soil invertebrates have received more attention because of their ecological importance. They represent a dominant part of the soil biomass and are soil engineers regulating important soil processes, notably fertilization. The release in soils of pollutants known for their persistence and/or their toxicity is a concern. Exposure of terrestrial species to pollutants that may alter genomic function has become an increasing topic of research in the last decade. Indeed, genome disturbances due to genetic and epigenetic mechanisms may impair growth, as well as reproduction and population dynamics in the long term. Despite their importance in gene expres- sion, epigenetic mechanisms are not yet understood in soil invertebrates. Until now, pollutant-induced changes in genome expression in natural biota are still being studied through structural alteration of DNA. The first biomarker relating to genotoxicant exposure in earthworms from multi-contaminated soils reported is DNA adducts measurements. It has been replaced by DNA breakage measured by the Comet assay, now more commonly used. Functional genomic changes are now being explored owing to molecular ＂omic＂ technologies. Approaches, objectives and results are overviewed herein. The focus is on studies dealing with genotoxicity and populational effects established from environmentally-relevant experiments and in situ studies [Current Zoology 60 （2）： 255-272, 2014].