Digestive enzymes type 1 diabetes vs,probiotics food meaning of,probiotics and reflux gerd,xymogen probiomax df - Downloads 2016

Abdominal bloating, constipation, or heartburn is a type of problem that everyone felt sooner or later in their digestive system. I agree to Shutterstock's Website Terms, Privacy Policy, Licensing Terms and to receive emails that I can opt out of at any time.
Progesterone is a steroid hormone involeved in regulating female menstrual cycle and pregnancy. Histamine is a hormone that regulates immune response, gut function and acts as neurotransmitter. All plans come as a Standard license, and can be upgraded to an Enhanced license at any time. This report contains the collective views of an international group of experts and does not necessarily represent the decisions or the stated policy of the United Nations Environment Programme, the International Labour Organization, or the World Health Organization.
Published under the joint sponsorship of the United Nations Environment Programme, the International Labour Organization, and the World Health Organization, and produced within the framework of the Inter-Organization Programme for the Sound Management of Chemicals. The International Programme on Chemical Safety (IPCS), established in 1980, is a joint venture of the United Nations Environment Programme (UNEP), the International Labour Organization (ILO), and the World Health Organization (WHO). The Inter-Organization Programme for the Sound Management of Chemicals (IOMC) was established in 1995 by UNEP, ILO, the Food and Agriculture Organization of the United Nations, WHO, the United Nations Industrial Development Organization, the United Nations Institute for Training and Research, and the Organisation for Economic Co-operation and Development (Participating Organizations), following recommendations made by the 1992 UN Conference on Environment and Development to strengthen cooperation and increase coordination in the field of chemical safety.
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Concise International Chemical Assessment Documents (CICADs) are the latest in a family of publications from the International Programme on Chemical Safety (IPCS) — a cooperative programme of the World Health Organization (WHO), the International Labour Organization (ILO), and the United Nations Environment Programme (UNEP). International Chemical Safety Cards on the relevant chemical(s) are attached at the end of the CICAD, to provide the reader with concise information on the protection of human health and on emergency action.
The primary objective of CICADs is characterization of hazard and dose-response from exposure to a chemical. Risks to human health and the environment will vary considerably depending upon the type and extent of exposure. While every effort is made to ensure that CICADs represent the current status of knowledge, new information is being developed constantly. Special emphasis is placed on avoiding duplication of effort by WHO and other international organizations. The first draft is usually based on an existing national, regional, or international review.
The second stage involves international peer review by scientists known for their particular expertise and by scientists selected from an international roster compiled by IPCS through recommendations from IPCS national Contact Points and from IPCS Participating Institutions.
Board members serve in their personal capacity, not as representatives of any organization, government, or industry. Board members, authors, reviewers, consultants, and advisers who participate in the preparation of a CICAD are required to declare any real or potential conflict of interest in relation to the subjects under discussion at any stage of the process.
This CICAD on glyoxal was prepared by the Fraunhofer Institute for Toxicology and Experimental Medicine, Hanover, Germany. The predominant target compartments for glyoxal in the environment are the hydrosphere and soil (at about 46% and 54%, respectively) and, to a lesser extent, air (<1%). Due to microbial activity as well as non-enzymatic autoxidation of oil or browning reactions of saccharides, glyoxal is frequently detected in fermented food and beverages.
Glyoxal released into the environment is rapidly converted by abiotic processes, such as transformation by photochemically produced hydroxyl radicals. The main routes of occupational exposure to glyoxal during use as a disinfectant are via inhalation of aerosol and dermal absorption.
Glyoxal is endogenously produced during normal cellular metabolism by a multitude of enzyme-independent pathways. Glyoxal, which attacks amino groups of proteins, nucleotides, and lipids, is considered an important intermediate in the formation of advanced glycation end-products (AGEs).
The acute toxicity of glyoxal in experimental animals is low to moderate, depending on the actual concentration of glyoxal in the tested product. In animal studies, 30% and 40% aqueous glyoxal caused slight to definite skin irritations, depending on the application time.
Glyoxal is directly genotoxic in vitro in bacterial and mammalian cells, inducing, for example, DNA adducts, mutations, chromosomal aberrations, DNA repair, sister chromatid exchanges, and DNA single strand breaks. In a sample risk assessment for the general population, an exposure scenario has been compiled as a hypothesized worst case. In the final sample risk assessment, a farmer using a spray application of biocidal products containing glyoxal to disinfect a stable was used as an example. A sample risk characterization for the aquatic environment was performed by calculating the ratio between a local predicted environmental concentration (PEC), based on recently measured data, and a corresponding predicted no-effect concentration (PNEC). The environmentally relevant physicochemical properties of glyoxal and of the commercially employed 40% aqueous solution of this compound are summarized in Table 1.
Accepted methods for the detection and quantification of glyoxal in different matrices are given below.
Determination of glyoxal in air usually involves concentration of the alpha-dicarbonyl onto a solid sorbent coated with an appropriate derivatization agent followed by solvent desorption prior to high-performance liquid chromatographic (HPLC) detection. Table 1: Physicochemical properties of glyoxal and its commercially employed aqueous solution (40%).
Edelkraut & Brockmann (1990) detected and quantified glyoxal in water samples by using the typical 2,4-DNPH derivatization followed by HPLC with diode array detection at 360 nm. The concentration of glyoxal in whole-blood samples was determined by derivatization with 1,2-diamino-4,5-dimethoxybenzene, solid-phase extraction, and HPLC of the resulting quinoxaline adduct with fluorometric detection (Thornalley et al., 1996).
Two well established processes employed for the production of glyoxal are the gas-phase oxidation of ethylene glycol with air in the presence of copper or silver catalysts at elevated temperature (about 300 °C) and the liquid-phase oxidation of acetaldehyde with nitric acid (Chumbhale & Awasarkar, 2001). Glyoxal is used as a chemical intermediate in the production of pharmaceuticals and dyestuffs. Even under physiological conditions, glyoxal reacts quickly with arginine, leading to the formation of 1-(4-amino-4-carboxybutyl)-2-imino-5-oxo-imidazolidine (Schwarzenbolz et al., 1997). The main route of exposure of the general population to glyoxal is probably via intake of water and food containing glyoxal.
Glyoxal has been reported as being present in some household cleaners up to a concentration of 4% (product databanks, Switzerland, Denmark, and Germany; R. A model calculation has been made using an aerosol droplet simulation programme for a worst-case exposure via inhalation of aerosol droplets — for example, of a farmer disinfecting his stable by spray application of a commercial product (see Appendix 5 for details).
In biological materials, less than 10% of the glyoxal present is in unbound forms in aqueous solution (free glyoxal and hydrates), as most of the reactive carbonyl groups are reversibly bound to cysteinyl, lysyl, and arginyl residues of proteins (Thornalley, 1995). The endogenous concentrations of glyoxal in human tissues and body fluids, as with other alpha-oxoaldehydes, are limited by the high catalytic efficiency of the glyoxalase system (Thornalley, 1995) as well as by the rapid reaction of glyoxal with proteins (Sady et al., 2000). There are limited qualitative and no quantitative data on the absorption and distribution of glyoxal in humans and experimental animals. The cytosolic GSH-dependent glyoxalase system is the major pathway for the detoxification of glyoxal (see Figure 1). Glyoxal attacks the amino groups of proteins, nucleotides, and lipids with its highly reactive carbonyl groups. AGEs originating from the reaction of glyoxal with lysine and arginine residues of proteins identified so far are Nε-(carboxymethyl)lysine (CML), imidazolium cross-links as glyoxal-lysine dimer and imidazolysine, arginine-derived imidazolium products, and arginine-lysine cross-links.
Glyoxal forms stable adducts with guanosine by reaction with the N-1 as well as with the exocyclic nitrogen of guanine.
Reaction of glyoxal with deoxycytidine (dC) yields 5-hydroxyacetyl-deoxycytidine or, by deamination, deoxyuridine.
Pancreas and kidney were identified as the prominent target organs of the toxic action of glyoxal; severe degenerative changes in these organs were attributed to an inhibition of glyoxalase activity in these tissues. A further study in rabbits described histopathological changes in liver, kidney, and pancreas 40 days after a single dermal application of a 40% glyoxal solution (leading to severe necrotic dermatitis at application site; dose not specified). In a 90-day feeding study, Wistar rats (10 males and 10 females per dose group) were exposed to glyoxal (40% preparation). There was a dose-dependent retardation of body weight gain, which was significant for the mid- and high-dose groups, and also a dose-dependent decrease of food and water intake.
Glyoxalase I activity was significantly increased in liver and erythrocytes at the mid- and high doses and in the kidneys at the high dose at the 30-day termination, but not for longer exposure periods. In the Salmonella microsomal assay, glyoxal (test substance 30-40% glyoxal) was a direct mutagen in strains TA 100, TA 102, TA 104, and TA 2638, with a weaker response in the presence of a metabolic activation system (BUA, 1997).
Furthermore, DNA repair tests yielded positive responses in both the presence and absence of metabolic activation systems, as in the SOS umu-test with S. DNA damage was further demonstrated in the comet assay with TK6 human lymphoblastoid cells by the induction of concentration-dependent increases of tail moment and tail length (Henderson et al., 1998). Glyoxal was demonstrated to be genotoxic at the site of application after administration by gastric intubation.
However this problem can be very disturbing for your activities, and at certain levels can damage your stomach and cause other conditions.
Affected part of your oesophagus removed and the healthy part reattached to your stomach, which the surgeon pulls up into the chest. Everyone who signs up gets full access to our entire library, including our curated collections. Our Standard license allows you to use images for anything, except large print runs over 500,000+ or for merchandising.
Once you have downloaded your image, you have life-long rights to use it under the terms of the license purchased. The overall objectives of the IPCS are to establish the scientific basis for assessment of the risk to human health and the environment from exposure to chemicals, through international peer review processes, as a prerequisite for the promotion of chemical safety, and to provide technical assistance in strengthening national capacities for the sound management of chemicals. The purpose of the IOMC is to promote coordination of the policies and activities pursued by the Participating Organizations, jointly or separately, to achieve the sound management of chemicals in relation to human health and the environment. Dotted lines on maps represent approximate border lines for which there may not yet be full agreement. Errors and omissions excepted, the names of proprietary products are distinguished by initial capital letters.

CICADs join the Environmental Health Criteria documents (EHCs) as authoritative documents on the risk assessment of chemicals.
They are usually based on selected national or regional evaluation documents or on existing EHCs. CICADs are not a summary of all available data on a particular chemical; rather, they include only that information considered critical for characterization of the risk posed by the chemical.
Responsible authorities are strongly encouraged to characterize risk on the basis of locally measured or predicted exposure scenarios. Unless otherwise stated, CICADs are based on a search of the scientific literature to the date shown in the executive summary. They are selected because of their expertise in human and environmental toxicology or because of their experience in the regulation of chemicals.
Representatives of nongovernmental organizations may be invited to observe the proceedings of the Final Review Board. It is based on reports compiled by the German Advisory Committee on Existing Chemicals of Environmental Relevance (BUA, 1997).
Due to the low soil sorption coefficient (Koc) reported for this compound, it may leach from soil into groundwater.
The general population is exposed mainly through ingestion of glyoxal-containing food, but could be exposed through polluted air in urban regions and through traces of glyoxal in drinking-water.
Glyoxal is also a product of the metabolism and microsomal oxidation of other compounds, such as glycolaldehyde, ethylene glycol, and beta-hydroxy-substituted N-nitrosamines. AGE modification alters protein function and inactivates enzymes, resulting in disturbance of cellular metabolism, impaired proteolysis, and inhibition of cell proliferation and protein synthesis. Glyoxal is irritating to mucous membranes and acts as a skin sensitizing agent in humans and experimental animals. In vivo, a genotoxic activity of glyoxal was established at the site of application in the pyloric mucosa of rats by demonstration of unscheduled DNA synthesis and DNA single strand breaks. As no additional data characterizing the toxic effects exhibited by glyoxal upon terrestrial microorganisms or invertebrates are available, it was not possible to perform a reliable quantitative risk characterization. Additional physical and chemical properties are presented in the International Chemical Safety Card reproduced in this document.
Additional and more detailed information is available in BUA (1997) and references cited therein. The interbatch coefficient of variation was 20%, the limit of detection 40 pmol, and the recovery 99%.
In Germany, less than 10 000 tonnes of glyoxal (40%) were produced in 1992 (BUA, 1997).
With respect to photolytic transformation (overhead sun), a lifetime of 5 h was calculated by the same author.
Intracellularly produced glyoxal readily crosses cell membranes, possibly by passive diffusion. Acute and subacute inhalation exposure resulted in local effects on eyes and respiratory organs, the extent of systemic absorption being unclear. However, this could either be produced endogenously or stem from an exogenous source, such as food intake.
Glyoxal reacts non-enzymatically with GSH with formation of a hemithioacetal, which is subsequently converted to S-glycolylglutathione by glyoxalase I. In human tissues, the specific activity was highest in pancreas, lung, kidney, and brain and lowest in adipose tissue and liver. A sequence of non-enzymatic reactions, called glycation, yields stable AGEs with a background extent of 0.1-1% of lysine and arginine residues in proteins and 1 in 107 nucleotides in DNA. The rate of glyoxal-guanine adduct formation is rapid under physiological conditions (Loeppky et al., 1999).
However, from the documentation in the study reports, it is not always clear if the values given for the LC50 or LD50 refer to the tested product with its specified concentration or if the values were converted to a concentration of 100% glyoxal.
Granular and vacuole degeneration in liver, kidney, and pancreas and atrophy and fibrous change of Langerhans islets were assessed to show a close resemblance to changes in these tissues in the course of diabetes. Exposure was tolerated by all dose groups without any systemic effects (examination of body weight, haematological and biochemical parameters, urine analysis, macroscopic and histological examination).
A dose-dependent retardation of body weight gain in the mid-dose group (slight effect) and the high-dose group (significant effect) was accompanied by reduced food intake. Up to the high dosage, no substance-related changes of body weight, food consumption, liver or kidney weight, or haematological or serum clinical chemistry parameters and no macroscopic or histopathological changes were observed in thoracic and abdominal organs (pancreas not examined).
From Phase II of this study (see below), it was concluded that body weight reduction did not correspond to decreased food intake but was a reflection of the systemic effects of glyoxal. One control group received food ad libitum, whereas a second diet-limited control group received the same amount of food as consumed by the dosed animals. All animals of the highest dose group were sacrificed prematurely on day 12 in a moribund state. Subsequent promotion by exposure to glyoxal (0.5% in drinking-water from week 8 to week 40) induced significantly increased incidences of adenocarcinoma and hyperplasia in the pylorus of the glandular stomach in comparison with rats with initiation treatment only. A direct genotoxic activity of glyoxal was further evident in the L-arabinose resistance assay with S.
In primary rat hepatocytes, glyoxal induced DNA single strand breaks but no DNA cross-links (Ueno et al., 1991c). However, from the increase of radiation-induced clastogenic effects after pretreatment with glyoxal, it was concluded that glyoxal came in contact with the target cells. It is important for you to recognize common problems and to do things that can help improve digestive health.
This is caused by the incoming air when eating or drinking rapidly and drinking carbonated beverages.
Eating broccoli, string beans, and carbonated drinks can cause bloating or abdominal discomfort. Gas is formed in the intestine due to the action of bacteria, which then protrudes from the anus.
Heartburn or acid reflux is caused by stomach acid spilling into esophagus and irritate the lining of the esophagus is unprotected.
So, if you want to be healthy, then you have to take good care of your body, and the digestive system is just as important. If at any time you're unsatisfied with your experience with us, you can cancel your subscription. They may be complemented by information from IPCS Poison Information Monographs (PIM), similarly produced separately from the CICAD process. Before acceptance for publication as CICADs by IPCS, these documents undergo extensive peer review by internationally selected experts to ensure their completeness, accuracy in the way in which the original data are represented, and the validity of the conclusions drawn.
The critical studies are, however, presented in sufficient detail to support the conclusions drawn. To assist the reader, examples of exposure estimation and risk characterization are provided in CICADs, whenever possible. In the event that a reader becomes aware of new information that would change the conclusions drawn in a CICAD, the reader is requested to contact IPCS to inform it of the new information. If the source document does not contain an environmental section, this may be produced de novo, provided it is not controversial.
Authors of the first draft are usually, but not necessarily, from the institution that developed the original review. Authors are required to take reviewers’ comments into account and revise their draft, if necessary.
Boards are chosen according to the range of expertise required for a meeting and the need for balanced geographic representation. Observers may participate in Board discussions only at the invitation of the Chairperson, and they may not participate in the final decision-making process. A comprehensive literature search of relevant databases was conducted up to February 2003 to identify any relevant references published subsequent to those incorporated in these reports.
However, it is generally available as an aqueous solution (typically containing 30-50% glyoxal) in which hydrated oligomers are present. However, it is readily biodegraded and quickly transformed enzymatically by bacteria and fungi.
The deleterious effects of the highly reactive glyoxal are counteracted by a ubiquitous glutathione (GSH)-dependent glyoxalase system, which converts glyoxal to the less reactive glycolate.
After inhalation exposure, local irritations of the eyes and respiratory organs as well as hyperaemia and foamy secretion in the lungs predominate. However, in 2002, BASF started up a new production plant with an annual capacity of about 60 000 tonnes (BASF AG, personal communication, 2003). In addition, emissions from cigarettes have been shown to contain trace amounts of glyoxal (Moree-Testa & Saint-Jalm, 1981). Therefore, a noteworthy transfer of glyoxal from the aqueous to the gas phase is not expected.
Li & Schlegel (2001) showed that the photofragmentation of glyoxal proceeded — under collision-free conditions — by internal conversion to a vibrationally excited state, which dissociates to yield H2 + CO + CO (28%), H2CO (formaldehyde) + CO (65%), and HCOH (hydroxycarbene) + CO (7%).
However, due to the lack of quantitative data on the presence of glyoxal in food products such as meat, dairy products, or fish, an exact value cannot be given.
Therefore, occupational exposure by inhalation will probably take place only in situations where aerosols containing glyoxal are released.
Glyoxalase II catalyses the hydrolysis of S-glycolylglutathione to glycolate, re-forming the GSH from the first reaction. Specific activities in fetal tissues were about 3 times higher than in corresponding adult tissues. A stable tricyclic glyoxal-DNA adduct is formed by covalent binding to two nitrogens of guanine under physiological conditions in vitro (for details, see BUA, 1997). The analysis of DNA bases involved in DNA cross-links formed in vitro showed cross-linking by deoxyguanosine-glyoxal-deoxycytidine adducts and deoxyguanosine-glyoxal-deoxyadenine adducts (Kasai et al., 1998). The glyoxal-induced rapid formation of CML showed the ability of the retina model to simulate AGE-related events in vitro. All rats survived 7- and 8-h exposures to concentrated atmospheres (concentration not further specified) of 30% (Mellon Institute, 1958, 1965) or 40% glyoxal (Hoechst AG, 1984d,e). A simultaneous increase of blood glucose levels was demonstrated in rabbits and cats, comparable to alloxan-induced diabetes (Doerr et al., 1948).

In glucose tolerance tests performed 5 and 10 days after dermal application of glyoxal, a distinct increase of blood glucose levels was observed in comparison with a constant level in control rabbits (Ito, 1963). The only local effect found in the larynx was a minimal squamous metaplasia of the epiglottal epithelium accompanied by a minimal submucosal infiltration of lymphocytes in the mid- and high-dose groups.
A dose-dependent reduction of water intake was observed in male rats at the lowest dose and in female rats at the mid- and high doses (glyoxal concentrations were adjusted to water intake).
Males of the high-dose group showed a reversible significant retardation of body weight gain during the first 2 weeks of exposure without a concomitant reduction of food intake. The study design included observations of clinical signs, body weights, major organ weights (liver, kidneys, spleen, heart, testes, brain), serum clinical chemistry, and biochemical examinations of glyoxalase activity and extent of lipid peroxidation (content of GSH and 2-thiobarbituric acid-reactive substances) in liver, kidneys, and erythrocytes.
Absolute weight of liver, kidneys, spleen, and heart significantly decreased in all dosed groups at all time points.
In the low-dose group, alanine aminotransferase and total protein were significantly decreased, so that it was not possible to derive a NOAEL for this study. Decreased dose-related body and organ weights as well as decreased food and water consumptions were observed at the lowest dosage. It was felt that the decreased water consumption (dose-dependently about 10-50%) was due to unsatisfactory palatability of the dosed water, subsequently leading to lower daily dosages and decreased feed consumption (up to 24%). Glyoxal treatment alone induced neither neoplastic nor hyperplastic changes in the pylorus (Takahashi et al., 1989).
A detailed overview of genotoxicity tests in bacterial test systems is published in the source document (BUA, 1997). Tail moment and the formation of comets with head and tail (indicative of DNA strand breakage) decreased with increasing glyoxal concentration, whereas circular DNA spots with highly condensed areas increasingly appeared at the mid- and high concentrations.
Try walking for 5-10 minutes and do not lie down after eating to help alleviate this problem. This condition usually occurs heartburn after eating spicy foods, fried foods, and fast food.
For additional information, the reader should consult the identified source documents upon which the CICAD has been based. These examples cannot be considered as representing all possible exposure situations, but are provided as guidance only. If no source document is available, IPCS may produce a de novo risk assessment document if the cost is justified.
The resulting second draft is submitted to a Final Review Board together with the reviewers’ comments.
Information on the preparation and peer review of the source document is presented in Appendix 1.
Glyoxal is used as a chemical intermediate in the production of pharmaceuticals and dyestuffs, as a cross-linking agent in the production of a range of different polymers, as a biocide, and as a disinfecting agent.
In biological materials, less than 10% of the glyoxal present is in unbound forms in aqueous solution (free glyoxal and hydrates), as most of the reactive carbonyl groups are reversibly bound to cysteinyl, lysyl, and arginyl residues of proteins.
After oral exposure to glyoxal, macroscopic observations include irritations of the gastrointestinal tract and congestion in the gastrointestinal tract, lung, kidney, and adrenal glands. Effects stated at higher dosages in these two latter studies were reduced water and food intake (first study only) and retardation of body weight gain (both studies). There is a perceived risk of local laryngeal effects and irritation to the skin from this spray application of glyoxal. As this is less than 1, no further information, testing, or risk reduction measures are required. Accordingly, Mopper & Stahovec (1986) detected the formation of glyoxal from humic acids by photochemical reactions in seawater. Hence, glyoxal released into the atmosphere will undergo a rapid degradation in this environmental compartment. The general population might also be exposed to glyoxal via cigarette or residential log fire smoke or vehicle exhaust containing glyoxal.
Such an exposure situation might be the spray application of biocidal products containing glyoxal.
This value is in apparent conflict with the low levels found in tissues and body fluids and with the assumed efficient glyoxalase activities in these patients. The activity of glyoxalase I in situ is approximately proportional to the cytosolic concentration of GSH. Human glyoxalase I was found to exhibit genetic polymorphism, with three phenotypes resulting from a diallelic gene. The neurotoxicity of glyoxal-induced AGE formation was shown by the significantly increased rate of cell death in the retina (Reber et al., 2003). After inhalative uptake, observations reported included local irritations of the eyes and respiratory organs as well as hyperaemia and foamy secretion in the lungs.
Macroscopic observations reported after oral uptake include irritations of the gastrointestinal tract and congestions in the gastrointestinal tract, lung, kidney, and adrenal glands (BUA, 1997). The pancreas is a prominent target organ of alloxan toxicity, too, which is mediated by free radicals (Younes, 1997). Changes in mid- and high-dose groups, such as increased erythrocyte number and reduced urine volume, were attributed to reduced water intake; changes of various organ weights in the high-dose group were attributed to reduced body weight. Significant increases of liver and kidney weights were observed in the high-dose group (these are the only organ weights examined). A significant increase of relative kidney weight in the high-dose group resulted after 90 days. The extent of examinations was comparable to that in Phase I and was further supplemented by gross and histopathological examinations of liver, kidneys, spleen, stomach, thymus, and mesenteric lymph nodes.
Among 100 tested substances, this damage was shown to be specific for certain aldehydes and was attributed to their DNA cross-linking activity (Kuchenmeister et al., 1998). In contrast, in rat hepatocytes, a test for unscheduled DNA synthesis was negative (CCR, 1992).
Gas formation in the stomach may occur because too much fiber in the diet and eating some foods, such as processed milk, broccoli, and cabbage.
Lie down immediately after eating; dehydration, smoking, and drinking alcohol can also lead to heartburn. The first draft undergoes primary review by IPCS to ensure that it meets the specified criteria for CICADs. At any stage in the international review process, a consultative group may be necessary to address specific areas of the science.
In the prominent target organs, pancreas and kidney, the toxic action of glyoxal leads to severe degenerative changes resembling those induced during diabetes.
Glyoxal showed tumour-promoting activity in a two-stage glandular stomach carcinogenesis model in male Wistar rats, whereas it was inactive in a short-term liver foci assay. Their results clearly indicated that glyoxal — as opposed to other biocides tested, such as formaldehyde — was not transferred from solution to the gas phase.
Granular and vacuole degeneration in liver, kidney, and pancreas have been observed along with a distinct increase in blood glucose levels following dermal application (Ito, 1963). No macroscopic organ changes were reported in those rats surviving the 14-day post-observation period (Hoechst AG, 1984d,e). No relevant macroscopic or micropathological changes were observed in thoracic and abdominal organs (pancreas not examined). Terminal body weight was significantly lower than in the pair-fed control, so that weight reduction is reflective of the systemic toxicity of glyoxal.
This CICAD was considered and approved as an international assessment at a meeting of the Final Review Board, held in Varna, Bulgaria, on 8-11 September 2003.
In an assay for tumour-initiating activity of glyoxal in skin and in cell transformation assays, glyoxal yielded negative test results.
However, glyoxal has to be regarded as a highly mobile compound in soil due to the low log Koc value (<1) reported (BUA, 1997). Hence, water or sewage treatment plants should be impacted detrimentally only at high influent concentrations.
A possible higher non-physiological production of glyoxal leading to local accumulation was assumed in patients with hyperglycaemia associated with diabetes (Akhand et al., 2001). Further, data on skin sensitization (see sections 8.7 and 9) provide supportive qualitative evidence that glyoxal is absorbed across the skin.
Significant decreases of absolute weights and significant increases of relative weights of liver, kidneys, and heart were observed in glyoxal-exposed rats (Ueno et al., 1991a). The scavengers of singlet oxygen almost completely suppressed the mutagenic action of glyoxal. FPG repairs oxidative DNA damage and abasic sites and further was supposed to repair guanine-glyoxal adducts (Shimoi et al., 2001).
Due to its excellent solubility in water and its low log Kow, it is not expected to bioaccumulate.
In fact, a large number of microbial enzymes catalyse the transformation of glyoxal to common intermediates in microbial catabolism. These levels did not significantly increase upon chlorine dioxide treatment of the raw water samples.
However, the B-cells of the pancreas showed the highest sensitivity to the toxic action of glyoxal (Helge, 1959).
The International Chemical Safety Card for glyoxal (ICSC 1162), produced by the International Programme on Chemical Safety (IPCS, 2002), has also been reproduced in this document.
Interestingly, glyoxal was detected as a minor species in turbulent flames of acetylene and ethylene under atmospheric pressure (Tichy et al., 1998). The nephrotoxic action of glyoxal is characterized by vacuole degeneration in the kidney (460 mg glyoxal per cat subcutaneous) (Doerr, 1957a,b).
Acute effects noted in the pancreas in several studies all seemed to arise when glyoxal was administered parenterally, compared with other routes. Glyoxal causes DNA single strand breaks in rat hepatocytes following in vitro and in vivo exposure (Ueno et al., 1991c).
Finally, the microbial glyoxalase system (Cooper, 1984) should yield glycolate in analogy to the reaction with methylglyoxal, whereas microbial aldehyde dehydrogenases with sufficient activity for 2-oxoaldehydes should yield glyoxylate.

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