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At least 19 recordsLinked to original sources

Medical aspects of environmental pollution. Environmental incidents in the Netherlands 1980-1984.

In the Netherlands since 1980, 16 situations have been identified in which man might be exposed to environmental pollutants. This paper provides an overview of these incidents and describes how health risk assessments, public studies and provision of individual medical toxicological care are dealt with. The importance of involving general practitioners and other primary health care personnel at an early stage is stressed.

Air Pollution↗

Role of bougainvilleas in mitigation of environmental pollution.

Environmental pollution adversely affects health of the people. Industrialization, urbanization, over exploitation of natural resources and increasing number of automobiles have aggravated the pollution manifold though there are various ways to mitigate the environmental pollution. Bio-remediation by using selected plant species is an effective method to control pollution which is universally accepted. Bougainvillea is a pollution tolerant plant and can help in the mitigation of air pollution besides its ornamental value in the landscaping. From the rich germplasm collection in NBRI Botanical Garden, tolerant plants have been experimented for road side plantation in view of mitigating the environmental pollution.

Air Pollutants↗

Molecular epidemiology studies of carcinogenic environmental pollutants. Effects of polycyclic aromatic hydrocarbons (PAHs) in environmental pollution on exogenous and oxidative DNA damage.

Exposure to high levels of environmental air pollution is known to be associated with an increased carcinogenic risk. The individual contribution to this risk derived from specific carcinogenic chemicals within the complex mixture of air pollution is less certain, but may be explored by the use of molecular epidemiological techniques. Measurements of biomarkers of exposure, of effect and of susceptibility provide information of potential benefit for epidemiological and cancer risk assessment. The application of such techniques has been mostly concerned in the past with the carcinogenic polycyclic aromatic hydrocarbons (c-PAHs) that are associated with particulate matter in air pollution, and has showed clear evidence of genotoxic effects, such as DNA adducts, chromosome aberrations (CA) and ras oncogene overexpression, in environmentally exposed Czech and Polish populations. We are currently extending these studies by an investigation of populations exposed to environmental pollution in three European countries, Czech Republic, Slovak Republic and Bulgaria. This pays particular attention to PAHs, but also investigates the extent of radically induced (oxidative) DNA damage in the exposed populations. Policemen, bus drivers and controls, who carried personal monitors to determine their exposures to PAHs have been studied, and blood and urine were collected. Antioxidant and dietary status were assessed in these populations. Stationary monitors were also used for ambient air monitoring. Amongst the parameters studied in the biological samples were: (a) exposure biomarkers, such as PAH adducts with DNA, p53 and p21(WAF1) protein levels, (b) oxidative DNA damage, (c) the biological effect of the exposure by measurement of chromosome damage by fluorescence in situ hybridisation (FISH) or conventional methods, and (d) polymorphisms in carcinogen metabolising and DNA repair enzymes. Repair ability was also measured by the Comet assay. In vitro systems are being evaluated to characterise the genotoxicity of the organic compounds adsorbed to air particles.

Biomarkers↗

[Environmental pollution--assessment of environmental medicine questionnaires and data in Schleswig-Holstein from 1995-1997].

Physicians qualified in environmental medicine due to their participation in special training courses in the federal state Schleswig-Holstein (Germany) may use a standardized questionnaire to report on their environmental medicine-related cases. The course of the illness and recovery, respectively, if known, is to be documented on a separate data sheet. During a three year period from 1995 to 1997 716 cases and 216 courses of illness and recovery, respectively, have been reported. The relevant environmental factors/toxicants of exposure most frequently documented by these physicians and found to be related to symptoms of illness were biocides (mainly insecticides used indoors for pest control, 31%) molds (30%), dental amalgam (28%), solvents or volatile organic compounds (VOC, 23%) and formaldehyde (17%), respectively. In 47% of the documented cases an exposure to more than one environmental factor/toxicant was registered. Age distribution as well as the symptoms of illness of the patients were found to be dependent on the type of exposure. After the physicians diagnosis of an environmental medicine-related illness the exposure was stopped completely in 57% of those cases of whom the course of the illness was known. Recovery was reported in 62% of these patients, and additional 30% had improved but had not recovered completely at the time of data-assessment. From these results it may be concluded that research work in the field of environmental medicine should be enforced in order to prevent unnecessary illness and to lower the costs of the public health system.

Adolescent↗

Risk forecasting and evaluating model of environmental pollution accident.

Environmental risk (ER) factors come from ER source and they are controlled by the primary control mechanism (PCM) of environmental risk, due to the self failures or the effects of external environment risk trigger mechanism, the PCM could not work regularly any more, then, the ER factors will release environmental space, and an ER field is formed up. The forming of ER field does not mean that any environmental pollution accident (EPA) will break out; only the ER receptors are exposed in the ER field and damaged seriously, the potential ER really turns into an actual EPA. Researching on the general laws of evolving from environmental risk to EPA, this paper bring forwards a relevant concept model of risk forecasting and evaluating of EPA. This model provides some scientific methods for risk evaluation, prevention and emergency response of EPA. This model not only enriches and develops the theory system of environment safety and emergency response, but also acts as an instruction for public safety, enterprise' s safety management and emergency response of the accident.

Accidents, Occupational↗

[Infectious morbidity in technogenic environmental pollution].

Technogenic environmental pollution has a marked indirect influence on the growth of infection morbidity. While comparing areas with different technogenic loads, the most significant differences in the levels of morbidity were noted in the period of minimal epidemic process intensity. This period was the most susceptible link of an epidemiological year.

Environmental Pollution↗

Peroxisome proliferation as a biomarker in environmental pollution assessment.

Peroxisome proliferators comprise a heterogeneous group of compounds known for their ability to cause massive proliferation of peroxisomes and liver carcinogenesis in rodents. In recent years it has become evident that other animals may be threatened by peroxisome proliferators, in particular aquatic organisms living in coastal and estuarine areas. These animals are exposed to a variety of pollutants of industrial, agricultural and urban origin which are potential peroxisome proliferators. Both laboratory and field studies have shown that phthalate ester plasticizers, PAHs and oil derivatives, PCBs, certain pesticides, bleached kraft pulp and paper mill effluents, alkylphenols and estrogens provoke peroxisome proliferation in different fish or bivalve mollusc species. The response appears to be mediated by peroxisome-proliferator activated receptors, members of the nuclear receptor family, recently cloned in fish. Based on these results it is proposed that peroxisome proliferation could be used as a biomarker of exposure to a variety of pollutants in environmental pollution assessment. This is illustrated by a case study in which mussels, used worldwide as sentinels of environmental pollution, were transplanted from reference to contaminated areas and vice versa. In mussels native to an area polluted with PAHs and PCBs, peroxisomal acyl-CoA oxidase (AOX) activity and peroxisomal volume density were 2-3 fold and 5-fold higher, respectively, compared to the reference site. When animals were transplanted to the polluted station, with increased concentration of organic xenobiotics, a concomitant significant increase of AOX was recorded. Conversely, in animals transplanted to the cleaner station, AOX activity and peroxisomal volume density decreased significantly. These results indicate that peroxisome proliferation is a rapid (i.e., two days) and reversible response to pollution in mussels. Before peroxisome proliferation can be implemented as a biomarker in biomonitoring programs, a well-defined protocol should be established and validated in intercalibration and quality assurance programmes. Furthermore, the influence of biotic and abiotic factors, some of which are known to affect peroxisome proliferation (season, tide level, interpopulation and interindividual variability), should be taken into consideration. The possible hepatocarcinogenic effects as well as the potential adverse effects on reproduction, development, and growth of peroxisome proliferators are unknown in aquatic organisms, thus providing a challenge for future investigations.

Acyl-CoA Oxidase↗

Are pharmaceuticals potent environmental pollutants? Part I: environmental risk assessments of selected active pharmaceutical ingredients.

As part of achieving national environmental goals, the Swedish Government commissioned an official report from the Swedish Medical Products Agency on environmental effects of pharmaceuticals. Considering half-lives/biodegradability, environmental occurrence, and Swedish sales statistics, 27 active pharmaceutical ingredients were selected for environmental hazard and risk assessments. Although there were large data gaps for many of the compounds, nine ingredients were identified as dangerous for the aquatic environment. Only the sex hormones oestradiol and ethinyloestradiol were considered to be associated with possible aquatic environmental risks. We conclude that risk for acute toxic effects in the environment with the current use of active pharmaceutical ingredients is unlikely. Chronic environmental toxic effects, however, cannot be excluded due to lack of chronic ecotoxicity data. Measures to reduce potential environmental impact posed by pharmaceutical products must be based on knowledge on chronic ecotoxic effects of both active pharmaceutical ingredients as well as excipients. We believe that the impact pharmaceuticals have on the environment should be further studied and be given greater attention such that informed assessments of hazards as well as risks can be done.

Drug Industry↗

Are pharmaceuticals potent environmental pollutants? Part II: environmental risk assessments of selected pharmaceutical excipients.

As part of achieving national environmental goals, the Swedish Government commissioned a report from the Swedish Medical Products Agency on environmental effects of pharmaceuticals and cosmetics and hygiene products. Five excipients used in pharmaceutical products were selected for environmental risk assessments, applying the computer-based model EUSES. Docusate sodium was identified as a possible risk for sediment-dwelling organisms when taking the total amount used into account. Although, experimental toxicity data on sediment-dwelling organism and data on concentrations in sediments are still required before firm conclusions regarding the environmental risk can be made. The environmental risks posed by excipients used in pharmaceutical products are likely to be negligible. This study identifies that knowledge gaps regarding environmental risks posed by pharmaceutical excipients are evident.

Drug Industry↗

Motorized exercise wheel for exposure of small animals to environmental pollutants.

For environmental inhalation studies a motorized exercise wheel was designed for small laboratory animals. Mice or hamsters were separated in individual enclosures, and each animal was required to perform the same exercise. The wheel was driven by a common barbecue spit motor, the speed of which may be varied by a standard variable transformer, from 1-6 revolutions per min. This unit can be adapted for a variety of laboratory applications.

Animals↗

Testing environmental pollutants on soil organisms: a simple assay to investigate the toxicity of environmental pollutants on soil organisms, using CdCl2 and nematodes.

Juvenile stages of Caenorhabditis elegans (nematoda) were isolated and grown in an axenic medium containing various concentrations of CdCl2. Growth of the organisms was significantly reduced from a level of 1 microM CdCl2. Reproduction of the nematodes was also reduced from that 1 microM exposure level. At levels of 160 and 320 microM, growth was retarded at the early juvenile stages and the organisms did not reach the adult stage and could therefore not reproduce. The test system turned out to be simple and reproducible and is therefore suitable for the investigation of the toxicity of compounds to soil nematodes.

Animals↗