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Control of diffuse P-pollutants by multiple buffer/detention structures by Yuqiao Reservoir, North China.

A case study on the transport process of agricultural diffuse P-pollutants was conducted in an experimental watershed locating in the north bank of Yuqiao Reservoir during 2001 and 2002. It was found that diversified artificial and natural buffer/detention landscape structures distributing along the ephemeral stream channel in this watershed played an important role of pollutants removal on downstream water quality, especially they have control effect on the diffuse P-pollutants transport process. Surface flow velocity was reduced sharply after passing through these structures. During continuous runoff events, the removal rate of TSS, TP, TDP, DRP by the whole system were 66.7%, 60.7%, 48.4%, and 43.3%, respectively. During discontinuous runoff events, removal rate of pollutants by the whole system was higher due to there was no or little surface water and pollutants exported from the watershed, of which removal rate of pollutants all exceeded 99% . The statistical analysis results of runoff events (n = 8) indicated that dry pond was the steadiest structure for controlling diffuse P-pollutants export.

Agriculture↗

[Coccidies genus Eimeria as a bioindicator of radioactive pollution of the biocenose].

The data on coccidies of rodents were collected in Chernobil (1989-1991) and in the regions of radioactive pollution in the Bryansk region of Russia (1992-1999). The surface pollution of experimental plots was different and come from 0.11 to 11.8 MBq/m2. 2185 rodent were examined in all. Thirteen types of coccidies p. Eimeria were found out in 525 small animals. The analysis of changes in morphological characters and oocysts sporulation in dependence of the level of radioactive pollution of biocenose was carried out. It was found out that parametric signs (length, width and form index of oocysts) were independent from radioactive pollution. At the some time the radioactive pollution renders a significant influence on the nonparametric signs (different types of capsule deformation and internal texture of oocysts) and the process of sporulation. With the increase of radioactive pollution the part of nonsporulated oocycts increased and the quantity of oocysts, corresponding to the description of given type (normal), decreased. This dependence is well described by the equation of logarithmic regression, that allows to use this indexes in the bioindication of the radioactive pollution of the biocenose.

Animals↗

[Air pollution in urban area in Cotonou and Lokossa, Benin].

In some African countries, time of clean environment with no air pollution belongs to the past. From now on, pollution is a problem of public heath in addition to malnutrition and infectious diseases still badly controlled. The sanitary consequences induced by pollution is now a cause for concern in the population. Yet, very few data are available to develop awareness of the population and convince the authorities to implement urgent policy in order to put a brake on the phenomenon. The objective of this document aims at describing the atmospheric pollution recorded in Cotonou and Lokossa as well as possible symptoms linked to exposure of pollutants of the population. Therefore we carried out a transversal study in the city of Cotonou and Lokossa (125 kilometers from Cotonou). Air samples were taken at crossroads levels and motorbikes to measure the different chemical components, 400 taxi drivers were questioned on symptoms affecting them. The toxicological analysis of air and blood sample is carried out at the laboratory of the Université Libre in Brussels. The data analysis revealed a high pollution in Cotonou. The carbon monoxide concentration varies from 26 ppm to 38,6 ppm in the morning and increases in the afternoon (58 to 78,6 ppm). Benzene is found with an average of 7,2 micro/m3 in Cotonou. These concentrations are not so high in the town of Lokossa (carbon monoxide from 45 to 51ppm). In Cotonou motorbike taxis account for 90% of the cases with intoxication symptoms 1,5 time higher than in the non-drivers of these motorbikes. The symptoms recorded on statement are intoxication disorders such as conjunctival hyperemia (18%) among which 12% of lacrimation, respiratory disorders (23%). On the other hand, registered disorders were not so important in Lokossa: conjunctival hyperemia (5,6%), nausea (32%) and other signs as sight disorders (4%). The disorders frequency in non drivers is not so high in Cotonou and Lokossa. In the blood test, the Hbco rate is abnormal in more than 66% of the drivers. The authors suggest the regular checking of imported secondhand cars, measures to reduce exhaust emissions and the reinforcement of the law on air pollution as well as a proper management of crossroads.

Adult↗

Immunoglobulins under the influence of nonspecific factors. III. Immunoglobulins, pertussis antibodies and lysozyme in three child populations exposed to different air pollution.

The levels of IgG, IgA, IgM, lysozyme, agglutinins against B. pertussis and B. parapertussis were followed in the blood serum of 306 children 9--10 years old in 3 areas of Central Bohemian region. In children dwelling in areas with more polluted air significantly higher levels of serum lysozyme and of parapertussis antibodies were found by the t-test. The distribution of these values shows significant differences between more polluted areas in comparison with lower-pollution area also in Kolmogorov-Smirnov test. The average levels of Ig approached statistically critical values but did not reach them, but significant differences in the distribution of values of IgG and IgA were shown by the F-test and chi2-test between lightly and heavily polluted areas. The values of immunological reactions in polluted areas were always higher than in the non-polluted group. This provides evidence for a hypothesis about a stimulatory effect of polluted air on immunological mechanisms in child population. The higher values of IgM observed recently by other authors in women were shown in girls of 9--10 years.

Agglutinins↗

Effects of environmental air pollution on the eye.

The eye is vulnerable to the effects of air pollution. Manifestations of air pollution can range from minimal or no symptoms to chronic discomfort and eye irritation. There may also be specific situations, in contact lens wearers for example, where the eyes may be adversely affected by air pollution. Despite the presence of air pollution in many indoor and outdoor environments, the ocular effects of air pollution are often overlooked by optometrists when examining their patients. In this article, background knowledge needed to understand the effects of air pollution on the eye will be reviewed. Suggestions for management of air pollution-related eye symptoms are provided.

Air Pollutants↗

A review of the toxicology of air pollutants: toxicology of chemical mixtures.

On a temporal basis, air has immense capacity for moving a large mass of pollutants. Mammals and birds are exposed to pollutants in air by the inhalation (nose and mouth), cutaneous or ocular routes. Most laboratory studies on air pollutants have been limited to single air pollutants and very little research has been done on the complex mixture of compounds that exist in ambient air. Complex mixtures are further complicated by dynamic chemical reactions that occur after the emissions leave point sources. Exposure parameters are also important in the toxicity of air pollutants. Intermittent exposure of monkeys to ozone increased the adverse pulmonary effects. Superimposing spikes of 0.8 ppm nitrogen dioxide on a baseline of 0.2 ppm, as occurs on a calm winter day, increased the susceptibility of mice to bacteria-induced pneumonia. Sulfur dioxide at concentrations of 5 ppm increased pulmonary resistance by 39%. Sulfuric acid is the predominate acid particle in the atmosphere. Exposure for 1 h to > 200 micrograms sulfuric acid/m3 depressed bronchomucociliary clearance. Concentrations of 100 micrograms/m3 of photochemical products caused headaches and 510 micrograms/m3 produced cough and chest pain. For chemical interactions in dose response, nitrogen dioxide is synergistic with ozone and ammonium sulfate. When all 3 chemicals are used in mixture, the response was 340%. Atmospheric conditions, such as fog, can alter the toxicity of air pollutants. The dose response to a single chemical can be altered by chemical mixtures and pre-existing disease conditions. Understanding these relationships is important for establishing no observable adverse effect levels. Mechanisms for multiple chemical interactions are multifaceted. One chemical may interfere with the metabolism or detoxification of another. Others may interact at cell receptors. To understand the effects of multiple chemical interactions of air pollutants, there is a need for a blend of epidemiological, laboratory and field studies. Studies are expensive. In the rural agricultural settings, the economic and environmental health risks are high. Should field observations and chemical problems be used as "red flags" for action?

Air Pollutants↗

Predictive pulmonary function of school children in an area of low air pollution in Taiwan.

The objective of this study was to determine the effect of different parameters on a predictive model of pulmonary function for elementary school children in an area of low air pollution in Taiwan. Healthy children aged 7 to 12 years from three elementary schools in low-air-pollution areas (Da-Chen, Mai-Liau and Tai-Si) participated in the study. A total of 836 children (423 boys and 413 girls) were included in the study. During summer vacation, each child underwent a physical examination including a screening spirometry. A questionnaire regarding respiratory symptoms and indoor air pollutants was also completed by the children's parents. Air monitoring showed that the levels of outdoor pollutants were relatively low. Multiple linear regression analysis was performed with FVC (forced vital capacity) and FEV1 (forced expiratory volume in 1 sec) as dependent variables. Gender, age, height, weight, technician and indoor air pollution parameters were the independent variables. The results showed that gender,height, weight and technician were the most significant variables for predicting FVC and FEV1. The various indoor air pollution parameters seemed to have no influence on the pulmonary function of children, except that mildew in bedrooms mildly decreased FEV1. Regression analysis showed that all the pulmonary function parameters measured had a positive correlation with height, whereas weight correlated only with certain parameters. Because both indoor and outdoor air pollution was relatively low, we suggest that this model could be used as a basic predictive model of pulmonary function for elementary school children in Taiwan.

Air Pollution↗

[Pneumological aspects of environmental medicine. Medical relevance of environmental pollution of outdoor air (1)].

The most important pollutants of industrial air pollution of the external air are sulfur dioxide (SO2), nitric oxides (NOX), oxygen radicals (ozone, O3) and sulfur dust. Brief detrimental effects on respiratory function of adults with healthy lungs are only observed during relatively high concentration of the pollutant, i.e. sulfur dioxide concentrations above 1500 micrograms/m3 or ozone 400 micrograms/m3. However, such a view of single pollutants is without medical relevance since all pollutants usually take effect as a pathological synergism in changing concentrations. Significant disturbances of the air ways may be found in sensitive persons (children, persons with air way problems, or cardiac and circulatory diseases) already after a slight increase in pollutant concentrations. It is assumed that the observed pollutant concentrations in the atmosphere close to the ground do not result in a permanent impact to health even under the circumstance of a combined effect.

Adult↗

The effects of different levels of air pollution on atopy and symptoms of allergic rhinitis.

We evaluated the prevalence of symptoms of allergic rhinitis and atopy among two groups living in areas with different pollution levels. The study was conducted among high school students living in Bayrampaşa (polluted by SO2 and TSP) and Beykoz (unpolluted, residential area) in Istanbul (n = 386). Each subject filled out a standardized self-administered questionnaire. Atopic status was evaluated by skin-prick testing using eight different allergens. Also, anterior active rhinomanometry was performed to evaluate the symptoms objectively. Significantly higher prevalence rates for symptoms of allergic rhinitis were found in Bayrampaşa (22.8%) compared to Beykoz (6%). However, no significant difference was found for atopic status among the two groups. When we evaluated the atopic status of subjects with symptoms of allergic rhinitis between the two areas, the prevalence of atopic students was found to be relatively higher in the unpolluted area (BZ). This difference was not statistically significant. Within the atopic population, subjects complaining of symptoms of allergic rhinitis were significantly more frequent in the polluted area (BP), suggesting that air pollution causes an increase in symptoms of allergic rhinitis in the atopic population, but this is not significantly higher than the increase in symptoms of allergic rhinitis of the total study group. Our results suggest that pollutants exert irritant effects on mucous membranes of the population in general rather than aggrevating symptoms in predisposed individuals. Smoking was more frequent in the unpolluted area. Exposure to parental smoking in childhood and heating systems in houses were evenly distributed. Household crowding was lower in Beykoz. Rhinomanometric measurements among the two groups did not show significant difference. Multiple logistic regression models estimating the role of each risk factor independently showed significant odds ratio associated with residence in Bayrampaşa for symptoms of allergic rhinitis (OR = 4.6, 95% CI = 9.0-2.3). In conclusion, this study suggests that outdoor pollution has adverse effects on the symptoms of allergic rhinitis, while it has no effect on the prevalence of atopy in Istanbul in the 1990s.

Adolescent↗

Managing respiratory effects of air pollution.

BACKGROUND: Exposure to air pollution (both indoor and outdoor) has many potential adverse effects on human health. OBJECTIVE: This article looks at the adverse respiratory health effects of air pollution and gives some guidance about management of exposure in susceptible individuals. DISCUSSION: Motor vehicle and industrial emissions are the primary contributors to outdoor air pollution in Australia. High levels of ozone and other pollutants can cause respiratory symptoms in susceptible individuals. Air quality advisory systems exist in most states. Clinicians can incorporate the health effects of air pollution, and awareness of advisory systems in the education of their susceptible patients and their carers. Asthma and chronic airways disease management plans should include provision for possible exposure to high pollution events and steps that can be taken to reduce exposure.

Air Pollutants↗

Enhanced biodegradation of aromatic pollutants in cocultures of anaerobic and aerobic bacterial consortia.

Toxic aromatic pollutants, concentrated in industrial wastes and contaminated sites, can potentially be eliminated by low cost bioremediation systems. Most commonly, the goal of these treatment systems is directed at providing optimum environmental conditions for the mineralization of the pollutants by naturally occurring microflora. Electrophilic aromatic pollutants with multiple chloro, nitro and azo groups have proven to be persistent to biodegradation by aerobic bacteria. These compounds are readily reduced by anaerobic consortia to lower chlorinated aromatics or aromatic amines but are not mineralized further. The reduction increases the susceptibility of the aromatic molecule for oxygenolytic attack. Sequencing anaerobic and and aerobic biotreatment steps provide enhanced mineralization of many electrophilic aromatic pollutants. The combined activity of anaerobic and aerobic bacteria can also be obtained in a single treatment step if the bacteria are immobilized in particulate matrices (e.g. biofilm, soil aggregate, etc.). Due to the rapid uptake of oxygen by aerobes and facultative bacteria compared to the slow diffusion of oxygen, oxygen penetration into active biofilms seldom exceeds several hundred micrometers. The anaerobic microniches established inside the biofilms can be applied to the reduction of electron withdrawing functional groups in order to prepare recalcitrant aromatic compounds for further mineralization in the aerobic outer layer of the biofilm. Aside from mineralization, polyhydroxylated and chlorinated phenols as well as nitroaromatics and aromatic amines are susceptible to polymerization in aerobic environments. Consequently an alternative approach for bioremediation systems can be directed towards incorporating these aromatic pollutants into detoxified humic-like substances. The activation of aromatic pollutants for polymerization can potentially be encouraged by an anaerobic pretreatment step prior to oxidation. Anaerobic bacteria can modify aromatic pollutants by demethylating methoxy groups and reducing nitro groups. The resulting phenols and aromatic amines are readily polymerized in a subsequent aerobic step.

Bacteria, Aerobic↗

Processes in Pollution Management: An Australian Model

/ This paper describes a model of the social and institutional processes involved in the solution of major pollution problems from the time they are first identified until they are resolved. The model is empirically demonstrated using four case studies of water and air pollution problems from Sydney, New South Wales, Australia. Each process of the model is quantified by the use of an indicator, e.g., number of articles in newspapers to measure the process "publicconcern," number of pages of text devoted to parliamentary debates to measure the process "political action." The case study data are presented on a time-line graph that shows the duration and magnitude of each process. The paper illustrates three aspects of the solution of major pollution problems: the long time frames involved, the importance of public opinion in initiating the solution process, and the partial nature of solutions-problems may be politically resolved but often a complete solution is not achieved. An understanding of social and institutional processes and time frames will enable planners and policy makers to communicate to the public and politicians the consequences of delay in acting to solve pollution and to direct attention to critical areas to expedite solutions.KEY WORDS: Pollution problems; Management process model; Performance indicators; Air pollution; Water pollution

Journal Article↗

Crop loss due to air pollution in The Netherlands.

The extent of yield reduction and economic loss caused by air pollution has been estimated for The Netherlands. Based on available data on direct effects only, each species was designated as sensitive, moderately sensitive or tolerant. On a nationwide scale, only ozone (O3), sulphur dioxide (SO2), and hydrogen fluoride (HF) exceeded effect thresholds. Effects from pollutant combinations were assumed to be additive. Yield reductions were calculated, using 10 exposure-response relationships and concentration data from the Dutch air pollution monitoring network. Changes in air pollution levels result in changes in supply. By multiplying the supply with the current price, the so-called crop volume was calculated. Subsequently, changes in crop volume were converted into economic terms, taking into account demand elasticity. On the basis of these calculations, air pollution in The Netherlands reduces total crop volume by 5%:3.4% by O3, 1.2% by SO2, and 0.4% by HF. The slope of the nonlinear relationship between crop volume reduction and exposure level increases at higher concentrations. In general, air pollution causes relatively little loss to producers, since yield reductions are largely compensated by higher prices. If air pollution in The Netherlands would be reduced to background concentrations, consumers would experience a net gain of Dfl 640 million (US 320 million dollars). Although large amounts of data were attained through literature and our own experience for this study, many assumptions still had to be made to arrive at these conclusions. With the current available knowledge, validation of our results in the field is not yet possible.

Journal Article↗

Atmospheric pollutants and ectomycorrhizae: more questions than answers?

Changes in research emphasis from pollution towards the effects of climate change have resulted from shifts in political and public interests. Information gained from research on the effects of pollutants as a perturbation on mycorrhizae and mycorrhizae-mediated processes may be an appropriate starting point from which to launch into climate change studies. However, the effects of pollution on mycorrhizae are not clear cut as there are many conflicting results. The methods used in experiments, levels of pollutants used and relationships between studies on seedling trees to the mature forest do not suggest unifying models of pollution effects. Some areas of work still lacking in the pollution field are highlighted. These include well replicated experiments at currently ambient pollutant levels, and areas for potential development in the global climate change arena, e.g. the interaction between C supply and nutrient uptake.

Journal Article↗

Studies on the progeny of rice plants grown at an unpolluted and polluted site.

Oryza sativa L. cv. GR3 was grown near to a fertilizer plant and the growth of its seed progeny was evaluated at sites near to, and distant from, the fertilizer plant. The grain yield was reduced in plants grown at the polluted site, with reduced panicle length and increased sterility index. This decrease in grain yield was higher in the progeny plants than in the normal polluted plants. The polluted progeny grown at a control site showed a normal yield, but an increased sterility index. Accumulation of total sulphur and fluoride was higher in the leaves of polluted rice plants. It was evident that tolerance to air pollution was reduced in the progeny plants due to an additional dosage of sulphur and fluoride pollutants and to unfavourable climatic factors. Further, pollution effects were not carried over in progeny plants when grown in an unpolluted environment.

Journal Article↗

Direct damage to vegetation caused by acid rain and polluted cloud: definition of critical levels for forest trees.

The concept of critical levels was developed in order to define short-term and long-term average concentrations of gaseous pollutants above which plants may be damaged. Although the usual way in which pollutants in precipitation (wet deposition) influence vegetation is by affecting soil processes, plant foliage exposed to fog and cloud, which often contain much greater concentrations of pollutant ions than rain, may be damaged directly. The idea of a critical level has been extended to define concentrations of pollutants in wet deposition above which direct damage to plants is likely. Concentrations of acidity and sulphate measured in mountain and coastal cloud are summarised. Vegetation at risk of injury is identified as montane forest growing close to the cloud base, where ion concentrations are highest. The direct effects of acidic precipitation on trees are reviewed, based on experimental exposure of plants to simulated acidic rain, fog or mist. Although most experiments have reported results in terms of pH (H(+) concentration), the accompanying anion is important, with sulphate being more damaging than nitrate. Both conifers and broadleaved tree seedlings showing subtle changes in the structural characteristics of leaf surfaces after exposure to mist or rain at or about pH 3.5, or sulphate concentration of 150 micromol litre(-1). Visible lesions on leaf surfaces occur at around pH 3 (500 micromol litre(-1) sulphate), broadleaved species tending to be more sensitive than conifers. Effects on photosynthesis and water relations, and interactions with other stresses (e.g. frost), have usually been observed only for treatments which have also caused visible injury to the leaf surface. Few experiments on the direct effects of polluted cloud have been conducted under field conditions with mature trees, which unlike seedlings in controlled conditions, may suffer a growth reduction in the absence of visible injury. Although leaching of cations (Ca(2+), Mg(2+), K(+)) is stimulated by acidic precipitation, amounts leached are small compared with root uptake, unless soils have been impoverished. This aspect of the potential effects of acidic precipitation is best considered in terms of the long-term critical-load of pollutants to the soil. Given the practical difficulties in monitoring cloud water composition, a method for defining critical levels is proposed, which uses climatological average data to identify the duration and frequency of hill cloud, and combines this information with measured or modelled concentrations of particulate sulphate in the atmosphere, to derive cloud water concentrations as a function of cloud liquid water content. For forests within 100 m of the cloud base the critical levels of particulate sulphate, corresponding to solution concentrations in the range 150-500 micromol litre(-1), are in the range 1-3.3 microg S m(-3). These concentrations are observed over much of central Europe, suggesting that many montane forests are at risk of direct effects of fossil-fuel-derived pollutants in cloud.

Journal Article↗

Conifer aphids in an air-polluted environment. I. Aphid density, growth and accumulation of sulphur and nitrogen by scots pine and Norway spruce seedlings.

The population dynamics of conifer aphids on pine and spruce seedlings growing in plastic pots were studied along a gradient from a pulp mill emitting mainly SO(2). At five locations, two apterous females of the grey pine aphid (Schizolachnus pineti L.) feeding on needles, and two apterous females of the spruce shoot aphid (Cinara pilicornis Hartig) feeding on the stem, were transferred to the leader shoot of 10 pine and spruce seedlings, respectively. The sulphur concentrations of the transplanted lichen Hypogymnia physodes (L.) Nyl. and needles of conifer seedlings were significantly increased in the close vicinity of the pulp mill. On pine seedlings, the numbers of S. pineti developed similarly at all study sites. However, in mid-July, the numbers of aphids started to decline near the emission source. In June, C. pilicornis reproduction on spruce was significantly faster at 0.2 and 0.5 km from the pollution source than at the more distant sites, but there was a rapid decline in aphid numbers in July. A negative correlation was observed between the numbers of C. pilicornis during the population peak in late June and the final length of the current year's leader shoot of spruce seedlings. Leader shoot growth of spruce seedlings infested by aphids was positively correlated with the distance from the pulp mill. There were no clear responses to pollution level in parasitization or predation rates of the aphids. The results suggest that all conifer aphids are not good indicators of pollution impact on conifers around a pollution source. There is a general agreement with the earlier reports that Cinara spp. numbers have a positive response to air pollution, especially to SO(2). This is probably due to promoted growth of nymphal aphids on the host plants suffering from pollution. However, high levels of air pollution may also cause rapid collapse of aphid populations. S. pineti, which lives on foliage, did not have a positive response to increased SO(2) levels.

Journal Article↗

The impact of livestock-farming on welsh streams: the development and testing of a rapid biological method for use in the assessment and control of organic pollution from farms.

Organic wastes from intensive agriculture are a major cause of surface-water pollution in Great Britain. There are a large number of possible sources for such pollution, and there is a need to target the efforts of pollution-control authorities to the worst-affected parts of catchments. This paper describes the development of a rapid method for the identification of polluted streams based upon the macro-invertebrate fauna. An indicator key was developed by TWINSPAN classification of data from benthic sampling at 55 sites in West Wales. The key requires assessment of the abundance of four macroinvertebrate taxa and of the extent of 'sewage-fungus' growth, all of which can be determined by examination in the field. The key can separate sites into three groups representing different levels of pollution impact as indicated by differences in biotic indices and chemical data. The system was tested successfully at a further 146 sites in West Wales resulting in the notification of 49 farms to the pollution-control authorities. Non-biologists were able to use the key efficiently after a short period of training. A further test involving 51 sites in Devon indicated that the technique may be adaptable to other parts of Great Britain. It is envisaged that indicator systems designed to suit local fauna may have a major role in a pro-active strategy developed to combat pollution from farms because they have potential advantages over more complex biological methods currently in use.

Journal Article↗