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Health and environmental impacts of increased generation of coal ash and FGD sludges. Report to the Committee on Health and Ecological Effects of Increased Coal Utilization.

This paper focuses on the incremental impacts of coal ash and flue gas desulfurization (FGD) wastes associated with increased coal usage by utilities and industry under the National Energy Plan (NEP). In the paper, 1985 and 2000 are the assessment points using the baseline data taken from the Annual Environmental Analysis Report (AEAR, September 1977). In each EPA region, the potential mix of disposal options has been broadly estimated and impacts assessed therefrom. In addition, future use of advanced combustion techniques has been taken into account. The quantities of coal ash and FGD wastes depend on ash and sulfur content of the coal, emission regulations, the types of ash collection and FGD systems, and operating conditions of the systems and boiler. The disposal of these wastes is (or will be) subject to Federal and State regulations. The one key legal framework concerning environmental impact on land is the Resource Conservation and Recovery Act (RCRA). RCRA and related Federal and State laws provide a sufficient statutory basis for preventing significant adverse health and environmental impacts from coal ash and FGD waste disposal. However, much of the development and implementation of specific regulations lie ahead. FGD wastes and coal ash and FGD wastes are currently disposed of exclusively on land. The most common land disposal methods are inpoundments (ponds) and landfills, although some mine disposal is also practiced. The potential environmental impacts of this disposal are dependent on the characteristics of the disposal site, characteristics of the coal ash and FGD wastes, control method and the degree of control employed. In general, the major potential impacts are ground and surface water contamination and the "degradation" of large quantities of land. However, assuming land is available for disposal of these wastes, control technology exists for environmentally sound disposal. Because of existing increases in coal use, the possibility of significant environmental impacts, both regionally and nationally, exists regardless of whether the NEP scenario develops or not. Existing baseline data indicate that with sound control technology and successful development and implementation of existing regulatory framework, regional scale impacts are likely to be small; however, site-specific impacts could be significant and need to be evaluated on a case-by-case basis. Both Federal and privately-funded programs are developing additional data and information on disposal of FGD sludges and coal ash. Continuation of these programs will provide additional vital information in the future. However, further information in several areas if desirable: further data on levels of radionuclides and trace metals in these wastes: studies on biological impacts of trace metals; and completion of current and planned studies on disposal problems associated with advanced combustion techniques like fluid bed combustion.

Coal

An investigation into the relationship between coal workers' pneumoconiosis and dust exposure in U.S. coal miners.

The National Study of Coal Workers' Pneumoconiosis (NSCWP) is a large, continuing epidemiologic study of the respiratory health of U.S. coal miners. By using information from the study, prevalence of coal workers' pneumoconiosis (CWP) was related to indexes of dust exposure obtained from research and compliance sampling data. Clear relationships between prevalences of both simple CWP and progressive massive fibrosis (PMF) and estimated dust exposure were seen. Additional effects independently associated with coal rank (% carbon) and age were also seen. Logistic model fitting indicated that between 2% and 12% of miners exposed to a 2-mg/m3 dust environment in bituminous coal mines would be expected to have Category 2 or greater CWP after a 40-yr working life; PMF would be expected for between 1.3% and 6.7%. The risks for anthracite miners appeared to be greater. There was a suggestion of a background level of abnormality, not associated with dust exposure, but increasing with age. Although there are certain weaknesses in the data used to derive these exposure estimates, the results are in general agreement with, but somewhat greater than, some recent findings for British coal miners.

Adult

[Study on the incidence of coal mine pneumoconiosis and lung cancer in Beijing coal mining district].

Thirty-two cases (20.13%) of primary lung cancer from 159 coal miner autopsies of Beijing coal mining area are reported in this study. The ratio of peripheral type to central type of lung cancer is 1.9:1; among them the adenocarcinoma is the most frequent (56.25%). Pathological examination shows that the diffuse interstitial type is the most common lung cancer. The occurrence of adenocarcinoma and the degree of lung fibrosis is related. The average number of ferruginous bodies is 190.2 +/- 8.06 in adenocarcinoma, 165.4 +/- 2.60 in squamous carcinoma, the difference is statistically significant (P < 0.05). The amount of trace elements-Fe, Al, Al/Si and Zn/Cu in lung with cancer is less than that without cancer. This article also discusses the relationship between coal mine pneumoconiosis with lung cancer of the formation of ferruginous bodies in the lung tissue of coal miner autopsies, which resembles the lung cancer combined with asbestosis. We also discussed the carcinogenesis of trace element in lung.

Adenocarcinoma

Environmental effects of increased coal utilization: ecological effects of gaseous emissions from coal combustion.

This report is limited to an evaluation of the ecological and environmental effects of gaseous emissions and aerosols of various types which result from coal combustion. It deals with NOx, SOx, fine particulate, photochemical oxidant and acid precipitation as these pollutants affect natural and managed resources and ecosystems. Also, synergistic effects involving two or more pollutants are evaluated as well as ecosystem level effects of gaseous pollutants. There is a brief summary of the effects on materials and atmospheric visibility of increased coal combustion. The economic implications of ecological effects are identified to the extent they can be determined within acceptable limits. Aquatic and terrestrial effects are distinguished where the pollutants in question are clearly problems in both media. At present, acid precipitation is most abundant in the north central and northeastern states. Total SOx and NOx emissions are projected to remain high in these regions while increasing relatively more in the western than in the eastern regions of the country. A variety of ecological processes are affected and altered by air pollution. Such processes include community succession and retrogression, nutrient biogeochemical cycling, photosynthetic activity, primary and secondary productivity, species diversity and community stability. Estimates of the non health-related cost of air pollutants range from several hundred million dollars to $1.7 billion dollars per year. In general, these estimates include only those relatively easily measured considerations such as the known losses to cultivate crops from acute air pollution episodes or the cost of frequent repainting required as a result of air pollution. No substantial nationwide estimates of losses to forest productivity, natural ecosystem productivity which is tapped by domestic grazing animals and wildlife, and other significant dollar losses are available.

Air Pollution

Biochemical decomposition of coal-tar dyes. II. Acute toxicity of coal-tar dyes and their decomposed products.

Twenty kinds of coal-tar dyes were subjected to median tolerance limit (TLm) test by use of Himedaka (Oryzias latipes) for the comparision of their acute toxicities. It became clear that 4 kinds of halogens substituted xanthene compounds dyes showed strong acute toxicities. From the fact that uranine had the lower acute toxicity than halogens substituted compounds and the toxicities of these 4 dyes increased through irradiation, it was assumed that halogen atoms in dyes might be responsible for these strong acute toxicities to fish.

Anaerobiosis

[Respiratory tract diseases in coal miners. II. Chronic non-specific respiratory tract diseases in coal miners].

Miners of two coal mines were examined: mine "A"--2094 miners and mine "B"--1846 miners working underground. Both the examined population and work environment were thoroughly described in part I. Medical examinations involved disease history and occupational inquiry on a special questionnaire form, a part of this questionnaire being based on the BMRC questionnaire. In addition, spirometric examinations were conducted, VC, FEV1 was determined, and chest was X-rayed. Average PNChUO rate in both populations under examinations came to 16.5%; in the "A" mine it was significantly higher (19.1%), compared to the "B" mine--(13.5%). Obturative PNChUO constituted, on average, 1.7% of the total PNChUO rate in both mines and occurred more frequently in the "B" mine (2.1%), where work was more mechanized than in the "A" mine (1.3%). The highest PNChUO percentage was found in those working at most dusted work--stands. The PNChUO rate in its obturative form was found to be directly proportional to age and length of employment. No effect of PNChUO on the quality and rate of changes in EKG in those suffering from this disease was found.

Adult

[Respiratory tract diseases in coal miners. III. Effects of smoking on the rate of chronic respiratory tract diseases in coal miners].

Effects of smoking on the case rate of chronic nonspecific respiratory tract diseases in underground coal miners of two mines "A" and "B" were analysed. Work environment and miners under investigation have been thoroughly described in Part I. Smoking miners from both mines, as examined using the significance test chi 2, did not differ significantly, as regards their age and length of employment. In either mine 73.7% of miners were smokers. In both groups of miners, smoking was found to largely affect health. The chronic nonsepcific respiratory tract diseases were 13 times more frequent in smokers and 11 times in ex-smokers, as compared to non-smokers. In smokers and ex-smokers the case rate of these diseases was found to be directly proportional to the amount of cigarettes smoked daily. The higest percentage of those diseases was found in smokers and ex-smokers smoking more than 25 cigarettes a day. The prevalence of chronic non-specific respiratory tract diseases was not increasing after more than 10 years of smoking. The obturative form of the disease came to about 10% in smokers and ex-smokers from both groups; thus it was 8 times more frequent than among general populations examined. In mine "A" non-smokers, the case rate of the disease was found to be almost twice that of mine "B", which may be indicative of additional factors promoting the development of chronic nonspecific respiratory tract diseases.

Chronic Disease

Studies on the toxicity of coal-tar dyes II. Examination of the biological reaction of coal-tar dyes to vital body.

The toxicity of xanthene dyes were studied by various interaction between the dyes and the components in vital body. (1) An increase in the amount of Rose Bengale adsorbed on the gill of fish was followed by the increase in red corpuscle number, and it was assumed that the death of fish in xanthene dye solution was due to anoxemia. (2) Binding capacity of xanthene dyes with bovine serum albumin decreased in the following; Rose Bengale, Phloxine, Erythrosine, Eosine and Uranine. This order was quite coincident with the toxicity compared by TLm values. (3) From the results of rec-assay test by use of Bacillus subtilis, it was confirmed that Phloxine and Rose Bengale had DNA-damaging capacity related to the mutagenecity.

Animals

Counteraction of poly(4-vinylpyridine-n-oxide) on the depression of viral interferon induction by coal dust.

The depressive activity of coal dust on interferon induction by influenza was markedly subverted when either coal dust or LLC-MK2 cell monolayers were pretreated with poly (4-vinylpyridine-N-oside). The polymer alone neither induced interferon synthesis, inhibited viral induction of interferon, influenced viral multiplication, nor affected cellular-induced resistance by interferon. Absorption of the polymer to coal dust not only occurred at a more rapid rate than to cell monolayers, but also less polymer was required to pretreat coal dust than cell monolayers to achieve comparable amelioration of interferon production. The polymer effectively negated the adverse activity of coal dust particles, irrespective of the latter's size (is less than 2.0 to 74.0 mum). Virus multiplication in the presence of coal dust=treated cell monolayers attained a level that was twofol higher than that noted with either polymer-pretreated coal dust or polymer-pretreated cell monolayers. Interferon production was almost completely inhibited in the presence of coal dust; pretreating coal dust or cells with the polymer abrogated this inhibitory activity of coal dust. It is tentatively suggested that coal dust particles per se directly interact with cell membranes to subvert interferon induction and that the formation of an absorbed polymerlayer on these complexes prevents their interaction.

Coal