Genotoxic effects of fly ash in bacteria, mammalian cells and animals

Gastrointestinal tract exposure to particles and DNA damage in animals: A review of studies before, during and after the peak of nanotoxicology

Humans ingest particles and fibers on daily basis. Non-digestible carbohydrates are beneficial to health and food additives are considered safe. However, titanium dioxide (E171) has been banned in the European Union because the European Food Safety Authority no longer considers it non-genotoxic. Ingestion of microplastics and nanoplastics are novel exposures; their potential hazardous effects to humans have been under the radar for many years. In this review, we have assessed the association between oral exposure to man-made particles/fibers and genotoxicity in gastrointestinal tract cells and secondary tissues. We identified a total of 137 studies on oral exposure to particles and fibers. This was reduced to 49 papers with sufficient quality and relevance, including exposures to asbestos, diesel exhaust particles, titanium dioxide, silver nanoparticles, zinc oxide, synthetic amorphous silica and certain other nanomaterials. Nineteen studies show positive results, 25 studies show null results, and 5 papers show equivocal results on genotoxicity. Recent studies seem to show null effects, whereas there is a higher proportion of positive genotoxicity results in early studies. Genotoxic effects seem to cluster in studies on diesel exhaust particles and titanium dioxide, whereas studies on silver nanoparticles, zinc oxide and synthetic amorphous silica seem to show mainly null effects. The most widely used genotoxic tests are the alkaline comet assay and micronucleus assay. There are relatively few results on genotoxicity using reliable measurements of oxidatively damaged DNA, DNA double strand breaks (γH2AX assay) and mutations. In general, evidence suggest that oral exposure to particles and fibers is associated with genotoxicity in animals.

An evaluation of the toxicological aspects and potential doses from the inhalation of coal combustion products

This paper reviews toxicological literature pertaining to coal combustion products (CCPs) inhalation and presents case studies on the inhalation of CCPs from the Kingston Fossil Plant area and from the Colbert Fossil Plant CCP landfill site. While most research regarding coal plant emissions focuses on fly ash, this article takes a holistic approach to examining not only emitted particulate matter such as fly ash, but also the theoretical calculated doses of landfilled CCPs. Furthermore, these doses are compared to in vitro and in vivo studies in order to highlight differences between laboratory-based studies and to emphasize the difficulty in extrapolating effects from inhalation exposures. In both case studies, fugitive emissions from the Kingston ash spill or the Colbert CCP-handling operations did not exceed any national ambient air quality standards or reference concentrations for individual components. Adverse effects such as mild pulmonary inflammation noted in the reviewed literature were in response to doses much higher than would be likely to occur in humans exposed to landfilled CCPs. We conclude that the doses for fugitive emissions calculated herein do not appear to be high enough to elicit a measurable adverse response in humans.

Mutagenicity of bitumen and asphalt fumes

The mutagenicity of asphalt fumes was tested with the Salmonella bioassays. The aim was to investigate if recycled additives modify the genotoxicity of emissions. Recycling of old asphalt is increasing, and we studied also the mutagenicity of emissions sampled during the re-use of asphalt. The composition of vapours and fumes were analysed by gas chromatography and by liquid chromatography. Bitumens containing coal fly ash (CFA) or waste plastics were heated to the paving temperatures in the laboratory. In the field, bitumen fumes were collected during paving of stone mastic asphalts (lime or CFA as a filler), remixing of stone mastic asphalt (lime or CFA as a filler), and of asphalt concrete. All the lab-generated vapour fractions were non-mutagenic. The particulate fractions were mutagenic with TA98 in the presence of the S9 activation. In addition, the lab-fumes from bitumen containing waste plastics were positive with both strains without S9. Only particulate fractions sampled in the field were tested. They were mutagenic with and without metabolic activation with both strains. The mutagenic potency of the field samples was higher than that of the lab-generated fumes without S9, and the remixing fumes were more mutagenic than the normal paving and lab-generated fumes with S9. The use of inorganic additive, CFA, did not change the mutagenicity of the fumes, whereas the organic additive, waste plastics, increased the mutagenicity of the laboratory emissions significantly.

Study of effects on haematological parameters of rabbits intratracheally exposed to coal fly ash

This study was undertaken to evaluate the effects of the inorganic constituents of coal on the haematological parameters of rabbits. Coal obtained from mines in Enugu, Nigeria was ashed at temperature of 900 degrees C and the ash was fractionated to obtain a size range of 4-5 microm mean particle diameter. Rabbits were exposed to 50, 100 and 200 mg per kilogram weight of the rabbits through intratracheal instillation. The exposure period was 14 days consecutively. Phosphate buffered saline was used as the carrier. Blood samples were collected on day 0, 2, 5, 8, 11, 14 immediately before fly ash administration and also on the seventh day after termination of administration (day 21). Haematological parameters (red blood cell, white blood cell, haemoglobin estimation and packed cell volume as well as platelet counts) were evaluated. Slight decreases in all the haematological parameters evaluated within the 3-week study period were generally observed. These decreases were not however found to be significant when subjected to the Analysis of Variance (ANOVA) test at 99 per cent confidence level. From the results of this study, the suitability of the bituminous coal as a fuel with minimal appropriate management is suggested.

Bone marrow micronucleus assay: a review of the mouse stocks used and their published mean spontaneous micronucleus frequencies

We have examined published negative control data from 581 papers on micronucleated bone marrow polychromatic erythrocytes (mnPCE) for differences in mean frequency and the frequency distribution profile among the mouse stocks used with the bone marrow micronucleus assay. For the 55 mouse stocks with published micronucleus assay data, the overall mean frequency is 1.95 mnPCE/1,000 PCE (1.95 mnPCE/1,000); for the 13 stocks most commonly used in the assay, it is 1.88 mnPCE/1,000. During the last 5 years, the mnPCE rate for these 13 major stocks has been 1.74 mnPCE/1,000. This current mean frequency is a substantial decrease from the mean of 3.07 mnPCE/1,000 observed for these 13 stocks for data published prior to 1981. Of the major stocks, the highest mean mnPCE negative control frequencies were observed for MS/Ae > BALB/c > C57Bl/6, and the lowest for CD-1 < Swiss Webster. We note that hybrid mouse stocks appear to have lower and less variable negative control frequencies than either of their parent strains and that the negative control frequency for some progeny stocks have diverged significantly from that of the parent stocks. Overall mean negative control frequencies appear to be correlated with breadth of the frequency distribution profile of published mean negative control values. Furthermore, a possible correlation between negative control frequency in the micronucleus assay and sensitivity to clastogens of different mouse strains may be indicated. The databases generated here allow us to define a range of norms for both the historical mean frequency and individual experimental mean frequencies for most stocks, but in particular, for the more commonly used mouse stocks. Our analysis, for the most part, bears out the recommendation of the first Gene-Tox Report on the micronucleus assay that the historical negative control frequency for a mouse stock should fall between 1 and 3 mnPCE/1,000. Eighty-six percent of the most commonly used mouse stocks have historical mean frequencies within this range. Though individual experimental mean values would not necessarily be expected to fall within the 1-3.00 mnPCE/1,000 range, 65.3% of the 2,327 published negative control values do, and 83.5% are < 3 mnPCE/1,000. The frequency with which an individual experimental mean value lies outside the 1.00 to 3.00 mnPCE/1,000 range differs among stocks and appears related to the mouse mean frequency. We suggest that the recommended range for historical mean frequency be extended slightly, to approximately 3.4 mnPCE/1,000, to accommodate some commonly used strains with overall mean negative control frequencies just above 3.00 mnPCE/1,000.(ABSTRACT TRUNCATED AT 400 WORDS)

Evaluation of exposure reducing measures on parameters of genetic risk in a population occupationally exposed to coal fly ash

In a previous study we found increased SCE frequencies in peripheral blood lymphocytes (PBLs) of workers occupationally exposed in a coal fly ash processing industry, as compared to a non-exposed control population. Shortly after this study, measures were taken in this plant to reduce fly ash levels. The objective of the present study, conducted 2 years later in the same plants, was to evaluate the effect of these measures with respect to genotoxic risk. A group of 18 male workers of the coal fly ash processing industry agreed to participate in the study. The control population consisted of 18 male workers from a flour processing industry, who were matched for age and smoking behavior. In contrast to our previous study, no increased SCE frequencies were found in PBLs of workers potentially exposed to coal fly ash when compared to the control group (mean SCEs: 6.4 +/- 1.2 and 7.0 +/- 0.9, respectively). In addition, no differences were observed between the exposed and control groups for frequencies of gene mutations at the hypoxanthine guanine phosphoribosyltransferase (hprt) locus in PBLs, for micronucleus frequencies using the cytokinesis block method, or for urinary mutagen excretion measured with Salmonella typhimurium tester strains TA98 and TA97 with and without metabolic activation. In smokers, however, SCE frequencies in PBLs were significantly increased in comparison to non-smokers (7.1 +/- 1.1 vs. 6.1 +/- 0.5; P < 0.005), as was 24-h urinary mutagen excretion measured with strain TA98 with S9 mix (2373 +/- 1870 vs. 156 +/- 211; P < 0.001) and with TA98 with S9 mix and beta-glucuronidase/arylsulfatase (2361 +/- 1958 vs. 538 +/- 396; P < 0.005). In addition, hprt variant frequencies in PBLs were higher in smokers than in non-smokers (15.0 +/- 23.5 x 10(-6)6 vs. 2.6 +/- 2.8 x 10(-6); P < 0.05). No differences were observed for micronucleus induction between smokers and non-smokers. It is concluded that the protective measures taken in the coal fly ash processing plant appear to have been sufficient, since an effect of exposure to coal fly ash on parameters of genetic risk was not found any longer.