Acrolein genotoxicity in Drosophila melanogaster. III. Effects of metabolism modification

Genotoxicity of lipid oxidation compounds

Lipid peroxidation, the oxidative degradation of membrane lipids by reactive oxygen species generates a large variety of breakdown products such as alkanes, aldehydes, ketones, alcohols, furans and others. Due to their reactivity aldehydes (alkanals, 2-alkenals, 2,4-alkadienals, 4-hydroxyalkenals) received a lot of attention, in particular because they can diffuse from the site of formation and interact with proteins and nucleic acids thus acting as second toxic messengers. The major aldehydic peroxidation product of membrane lipids is 4-hydroxynonenal (HNE). Since HNE and other 4-hydroxyalkenals are strong alkylating agents they have therefore been considered to be the biologically most important peroxidation products. Although initially research focused on the toxicological potential of these compounds it is now well known that they play also a crucial role in cell signaling under physiological and pathophysiological conditions. Thus, it is obvious that the biological effects will be determined by the intracellular concentrations which can trigger adaptation, DNA damage and cell death. This review will not cover all these aspects but will concentrate on the genotoxic properties of selected lipid oxidation products important in the context of pathophysiological developments together with a chapter on epigenetic modifications.

A comparative 90-day toxicity study of allyl acetate, allyl alcohol and acrolein

Allyl acetate (AAC), allyl alcohol (AAL), and acrolein (ACR) are used in the manufacture of detergents, plastics, pharmaceuticals, and chemicals and as agricultural agents. A metabolic relationship exists between these chemicals in which allyl acetate is metabolized to allyl alcohol and subsequently to the highly reactive, alpha,beta-unsaturated aldehyde, acrolein. Due to the weaker reactivity of the protoxicants, allyl acetate and allyl alcohol, relative to acrolien we hypothesized the protoxicants would attain greater systemic exposure and therefore deliver higher doses of acrolein to the internal organs. By extension, the higher systemic exposure to acrolein we hypothesized should lead to more internal organ toxicity in the allyl acetate and allyl alcohol treated animals relative to those treated with acrolein. To address our hypothesis we compared the range of toxicities produced by all three chemicals in male and female Fischer 344/N rats and B6C3F1 mice exposed 5 days a week for 3 months by gavage in 0.5% methylcellulose. Rats (10/group) were dosed with 0-100mg/kg allyl acetate, 0-25mg/kg allyl alcohol, or 0-10mg/kg acrolein. Mice (10/group) were dosed with 0-125mg/kg allyl acetate, 0-50mg/kg allyl alcohol, or 0-20mg/kg acrolein. The highest dose of allyl acetate and acrolein decreased survival in both mice and rats. The primary target organ for the toxicity of all three chemicals in both species and sexes was the forestomach; squamous epithelial hyperplasia was observed following exposure to each chemical. In both species the highest allyl acetate dose group exhibited forestomach epithelium necrosis and hemorrhage and the highest dose of acrolein led to glandular stomach hemorrhage. Liver histopathology was the most apparent with allyl acetate, was also observed with allyl alcohol, but was not observed with acrolein. All chemicals had effects on the hematopoietic system with allyl acetate having the most pronounced effect. When dosed at quantities limited by toxicity, allyl acetate and allyl alcohol produce higher levels of urinary mercapturic acids than the minimally toxic dose of acrolein. This observation is likely due to biotransformation of allyl acetate and ally alcohol to acrolein that occurs after absorption and suggests that these chemicals are protoxicants that increase systemic exposure of acrolein. Increased systemic exposure to acrolein is likely responsible for the differences in hepatic toxicological profile observed with these chemicals.

Reactive carbonyls and oxidative stress: potential for therapeutic intervention

Reactive aldehydes and ketones are produced as a result of oxidative stress in several disease processes. Considerable evidence is now accumulating that these reactive carbonyl products are also involved in the progression of diseases, including neurodegenerative disorders, diabetes, atherosclerosis, diabetic complications, reperfusion after ischemic injury, hypertension, and inflammation. To counter carbonyl stress, cells possess enzymes that can decrease aldehyde load. These enzymes include aldehyde dehydrogenases (ALDH), aldo-keto reductases (AKR), carbonyl reductase (CBR), and glutathione S-transferases (GST). Some of these enzymes are inducible by chemoprotective compounds via Nrf2/ARE- or AhR/XRE-dependent mechanisms. This review describes the metabolism of reactive carbonyls and discusses the potential for manipulating levels of carbonyl-metabolizing enzymes through chemical intervention.

Alkylpurine-DNA-N-glycosylase excision of 7-(hydroxymethyl)-1,N6-ethenoadenine, a glycidaldehyde-derived DNA adduct

Glycidaldehyde (GDA) is a bifunctional alkylating agent that has been shown to be mutagenic in vitro and carcinogenic in rodents. However, the molecular mechanism by which it exerts these effects is not established. GDA is capable of forming exocyclic hydroxymethyl-substituted etheno adducts on base residues in vitro. One of them, 7-(hydroxymethyl)-1,N6-ethenoadenine (7-hm-epsilonA), was identified as the principal adduct in mouse skin treated with GDA or a glycidyl ether. In this work, using defined oligonucleotides containing a site-specific 7-hm-epsilonA, the human and mouse alkylpurine-DNA-N-glycosylases (APNGs), responsible for the removal of the analogous 1,N6-ethenoadenine (epsilonA) adduct, are shown to recognize and excise 7-hm-epsilonA. Such an activity can be significantly modulated by both 5' neighboring and opposite sequence contexts. The efficiency of human or mouse APNG for excision of 7-hm-epsilonA is about half that, or similar to the excision of epsilonA, respectively. When human or mouse cell-free extracts were tested, however, the extent of 7-hm-epsilonA excision is dramatically lower than that for epsilonA, suggesting that, in the crude extracts, the APNG activities toward these two adducts are differentially affected. Using cell-free extracts from APNG deficient mice, this enzyme is shown to be the primary glycosylase excising 7-hm-epsilonA. A structural approach, using molecular modeling, was employed to examine how the structure of the 7-hm-epsilonA adduct affects DNA conformation, as compared to the epsilonA adduct. These novel substrate specificities could have both biological and structural implications.

Relationships between cell density, glutathione and proliferation of A549 human lung adenocarcinoma cells treated with acrolein

Acrolein is a highly electrophilic alpha,beta-unsaturated aldehyde to which humans are exposed in various situations. Acrolein reacts rapidly with and depletes cellular glutathione (GSH), and is toxic to various types of cells. In the current study, the ability of acrolein to alter proliferation of A549 cells was found to be dependent on cell density as well as total cell number. Thus, 'doses' must be expressed per cell rather than as a concentration, and all related studies need to be performed by plating a constant number of cells. A549 cells were plated at various densities and treated with acrolein after 48 h. Acrolein doses up to 47 fmol/cell at the time of treatment did not cause cell lethality. However, growth of A549 cells (as shown by thymidine incorporation, alamarBlue and total protein) was inhibited at acrolein levels > 34 fmol/cell in 6-well plates seeded at 5000 cells/cm2 48 h prior to treatment. Cellular GSH levels were decreased 34% by 2 h at acrolein levels of 6.7 fmol/cell and by 65% at 47 fmol/cell. Recovery of GSH was rapid at 6.7-47 fmol/cell acrolein, returning to control levels or above by 12 h post-treatment. These data show a strong correlation between cellular GSH and proliferation. The apparent conflict with a previous study of Ramu et al., suggesting that sublethal concentrations (up to 10 microM) of acrolein inhibited the proliferation of A549 cells without a decline in total cellular GSH, arose because, while the acrolein concentration was the same in cells used for proliferation and GSH assays, GSH measurements were done in cells plated at a higher density, resulting in a much lower acrolein dose per cell. Interestingly, very low dose levels of acrolein with cells seeded at low densities stimulated cell growth despite an initial decline in GSH content. Preliminary studies with the stress genes hsp70 and gadd153 suggest that acrolein at 35 fmol/cell does not stimulate formation of their mRNA beyond the level stimulated by a 2 h incubation in serum-free medium but may actually delay or decrease the induced expression. The mechanism(s) of the inhibitory and mitogenic effects of acrolein remains to be determined, but could be due to changes in gene expression induced by this electrophile, perhaps mediated by changes in GSH.

Fate and effects of acrolein

Acrolein is a highly toxic, reactive, and irritating aldehyde that occurs as a product of organic pyrolysis, as a metabolite of a number of compounds, and as a residue in water when used for the control of aquatic organisms. It is an intermediate in the production of acrylic acid, DL-methionine, and numerous other agents. Its major direct use is as a biocide for the control of aquatic flora and fauna. It is introduced to the environment from a variety of sources, including organic combustion such as automobile exhaust, cigarette smoke, and manufacturing and cooking emissions, as well as direct biocidal applications. Organic combustion from both fixed and mobile sources is the significant source of acrolein in the atmosphere; it represents up to 8% of the total aldehydes generated from vehicles and residential fireplaces and 13% of total atmospheric aldehydes. This reactive aldehyde also occurs in organisms as a metabolite of allyl alcohol, allylamine, spermine, spermidine, and the anticancer drug cyclophosphamide, and as a product of UV radiation of the skin lipid triolein. Furthermore, small amounts are found in foods; when animal or vegetable fats are overheated, however, large amounts are produced. Most human contact occurs during exposure to smoke from cigarettes, automobiles, industrial processes, and structural and vegetation fires. Besides cigarette smoke, occupational exposures are a common mode of human contact, particularly in industries that involve combustion of organic compounds. Firefighters, in particular, are exposed to extremely high levels during the extinguishment and overhaul phases of their work. Water may contain significant levels of the herbicide. It has been found in paper mill and municipal effluents at 20-200 micrograms/L, and at 30 micrograms/L as far as 64 km downstream from the point of application. The USEPA-recommended water quality criteria for freshwater are only 1.2 micrograms/L (24-hr avg) and 2.7 micrograms/L (maximum ceiling). Acrolein is highly reactive, and intercompartmental transport is limited. However, it is eliminated from aqueous environments by volatilization and hydration to beta-hydroxypropanal, after which biotransformation occurs, with a half-life of 7-10 d. The Koc for acrolein is 24, and it is not likely to be retained in soil; activated carbon adsorbs only 30% from solution. Thus, the aldehyde is either leached extensively in moist soil or volatilizes quickly from dry soil. It is eliminated from air by reaction with .OH (half-life, 0.5-1.2 d), NOx (half-life, 16 d), and O3 (half-life, 59 d), as well as by photolysis and wet deposition. As expected from its high water solubility, bioaccumulation is low. Acrolein is highly toxic by all routes of exposure. The respiratory system is the most common target: exposure causes localized irritation, respiratory distress, pulmonary edema, cellular necrosis, and increased susceptibility to microbial diseases. Additionally, acute inhalation studies verify that it is a severe respiratory irritant that affects respiratory rates. Respiratory rate depression may have a protective effect by minimizing vapor inhalation, thereby explaining the subadditive effect of acrolein when combined with the other toxic combustion by-products CO and HCHO. Liquid contact with the skin and eyes causes severe irritation, opaque or cloudy corneas, and localized epidermal necrosis, but no allergic contact dermatitis. The cardiovascular system is affected, resulting in increased blood pressure, platelet aggregation, and quick cessation of beating in perfused rat hearts. It may also inhibit mitochondrial oxidative phosphorylation in the myocardium. Acute LD50s and LC50s are low. Levels are 7-46 mg/kg and 18-750 mg/m3, respectively, in rats; aquatic organisms are affected above 11.4 micrograms/L.(ABSTRACT TRUNCATED)