Geochemistry and pollution.

During the past 7 years, the National Science Foundation-Research Applied to National Needs (R.A.N.N.) programme has supported extensive interdisciplinary research concerned with Pb, Cd and other hazardous trace metals. Various aspects of geochemistry and pollution research at the universities of Missouri, Illinois, Colorado State and Purdue are presented and summarized. The transport, pathways and distribution of Pb, Cd and other trace metals are discussed and the utilization of research findings by government and state agencies for the development of standards and by industries for pollution control are presented.     

Speciation of trace element compounds in samples of biota from marine ecosystems

Abstract

The toxicity, mobility, bioavailability and bioaccumulation of metals are dependent on the particular physico-chemical form in which the element occurs in the environment. Special attention has been paid to metals which are essential for the proper functioning of organisms if present in appropriate amounts but are toxic if in excess (i.e. Se, Cr), and also to non-essential elements (i.e. Hg, Pb, Cd, Sn and As). To assess the potential hazard to the health of marine organisms, qualitative and quantitative analyses of metal species accumulating along the food chain needs to be carried out. This paper reviews the available information on the speciation of trace elements in the food chain in marine ecosystems and the analytical tools used for acquiring reliable information in this field. Advantages and limitations of commonly used techniques indicate that all metal species in different samples need diverse extraction, separation and detection conditions. Although not recommending which procedure is the most suitable to determine a given compound, speciation analysis has the potential to be a powerful tool for the identification of trace element species in biological samples.     

Molecular mechanisms underlying the toxicity and detoxification of trace metals and metalloids in plants

Plants take up a wide range of trace metals/metalloids(hereinafter referred to as trace metals)from the soil,some of which are essential but become toxic at high concentrations(e.g.,Cu,Zn,Ni,Co),while others are non-essential and toxic even at relatively low concentrations(e.g.,As,Cd,Cr,Pb,and Hg). Soil contamination of trace metals is an increasing problem worldwide due to intensifying human activities.Trace metal contamination can cause toxicity and growth inhibition in plants,as well as accum...     

Low-molecular weight organic acids and peptides involved in the long-distance transport of trace metals

Higher plants evolved mechanisms of uptake, distribution and accumulation of trace metals essential for the proper functioning of the organism (e.g., copper, zinc). Non-essential metals (e.g., cadmium, arsenic, lead) can also enter plant cells using the routes dedicated to the essential ones, because of the shared similar chemical and physical properties. Generally, trace elements are very reactive, able to generate reactive oxygen species and to interact or bind various organic ligands composed of C, H, O, N, P or S. Thus, after entering to the cells, metals are transported and sequestered mainly in a complex form, bound with amino acids, organic acids, peptides or specific metal-binding ligands. Considering diverse properties (e.g., pH value, abundancy of ions, redox state) characterizing cells, tissues and phloem or xylem sap, plants use various ligands to form stable complexes in different conditions. This literature review aims to provide a comprehensive overview on the role of low-molecular weight acids and peptides in trace metals translocation.     

How Plants Cope with Cadmium: Staking All on Metabolism and Gene Expression

Environmental pollullon is one of the major problems for human health. Toxic heavy metals are normally present as soil constituents or can also be spread out in the environment by human activity and agricultural techniques. Soil contamination by heavy metals as cadmium, highlights two main aspects: on one side they interfere with the life cycle of plants and therefore reduce crop yields, and on the other hand, once adsorbed and accumulated into the plant tissues, they enter the food chain poisoning animals and humans. Considering this point of view, understanding the mechanism by which plants handle heavy metal exposure, In particular cadmium stress, is a primary goal of plant-blotechnology research or plant breeders whose aim is to create plants that are able to recover high amounts of heavy metals, which can be used for phytoremediation, or identify crop varieties that do not accumulate toxic metal in grains or fruits. In this review we focus on the main symptoms of cadmium toxicity both on root apparatus and shoots. We elucidate the mechanisms that plants activate to prevent absorption or to detoxify toxic metal ions, such as synthesis of phytochelatins, metallothioneins and enzymes involved in stress response. Finally we consider new plant-biotechnology applications that can be applied for phytoremediation.     

How Plants Cope with Cadmium: Staking All on Metabolism and Gene Expression

Environmental pollullon is one of the major problems for human health. Toxic heavy metals are normally present as soil constituents or can also be spread out in the environment by human activity and agricultural techniques. Soil contamination by heavy metals as cadmium, highlights two main aspects: on one side they interfere with the life cycle of plants and therefore reduce crop yields, and on the other hand, once adsorbed and accumulated into the plant tissues, they enter the food chain poisoning animals and humans. Considering this point of view, understanding the mechanism by which plants handle heavy metal exposure, In particular cadmium stress, is a primary goal of plant-blotechnology research or plant breeders whose aim is to create plants that are able to recover high amounts of heavy metals, which can be used for phytoremediation, or identify crop varieties that do not accumulate toxic metal in grains or fruits. In this review we focus on the main symptoms of cadmium toxicity both on root apparatus and shoots. We elucidate the mechanisms that plants activate to prevent absorption or to detoxify toxic metal ions, such as synthesis of phytochelatins, metallothioneins and enzymes involved in stress response. Finally we consider new plant-biotechnology applications that can be applied for phytoremediation.     

Health effects of natural dust

This article reviews the health effects of trace elements carried in natural dusts of geologic or geochemical origin. The sources of these dusts are diverse, including volcanoes, dust storms, long-range transport of desert dust, and displacement through natural processes such as landslides and earthquakes. The primary focus is dust exposures affecting communities rather than occupational groups (which have been comprehensively explored in other publications). The principal elements and compounds reviewed are trace metals (including As, Hg, Cd, and Fe), radioactive elements, fluoride, silicates, natural asbestiform compounds, and alkali salts. The pathways by which such agents affect human populations are explored, including carriage through water, air, soil, and the food chain. The mechanisms of biotoxicity and the acute and chronic consequences on health associated with these elements are described. The discussion explores problems inferring risk and disease causation from natural dust exposures using standard epidemiological indicators, particularly for chronic outcomes, and will argue for the importance of the ecological perspective in assessing pathogenesis. The authors stress the global scale of the problem, which remains underevaluated and underreported in terms of health implications.     

Definitions and principles for bioindication and biomonitoring of trace metals in the environment

Clear-cut definitions are given for most terms used in monitoring studies. In these studies the observation or experimental investigation of living organisms give a qualitative or quantitative information on the state of the environment with special reference to trace metals. The focus and future goals of biogeochemical research must consider the direct effects on human health, by including modelling of active biogeochemical processes than they have done so far. Newly developed strategies as the multi-markered bioindication concept (MMBC) with its functional and integrated windows on prophylactic healthcare are essential tools for successfully observing the environment with respect to trace metals. An intensified training of students and a strong hand in hand work between industrial, educational and public institutions is necessary.     

TRACE METAL CYCLING IN THE U.S. COASTAL ZONE: A SYNTHESIS

This synthesis of trace element research in estuarine communities of the U.S. coastline and the Caribbean provides a summary applicable to the shoreline of the tropical and temperate regions of the world which have mangroves, kelp beds, riverine marshes and seagrass communities. An inventory of sediments and leaf tissues shows Mn and Fe to be the most highly concentrated elements with Hg and Cd present in lowest concentrations. Generally, trace element concentrations in roots are much higher than in leaves and other tissues above the sediment. Tissue to sediment concentration ratios show that Cd is most likely to be bioamplified and that Cu, Hg, Sr and Zn may have relatively high concentration ratios which can exceed unity. A conceptual model was constructed to integrate the forcing functions, compartmental couplings, and dynamics common to these estuarine systems. Seasonality is important for changes in some trace element concentrations in plants and litter. Trace element additions to water or sediment increased certain trace element concentrations in plants and dead organic matter. It is clear that estuarine plant communities serve as living filters of estuarine trace elements. However, increased knowledge of trace element cycling in estuarine systems and relationships between trace element concentrations in plants and the estuarine food chain is needed, particularly food chains to man. There is a need for structured long-term estuarine research to allow direct comparison of results among estuarine study sites, to identify the similarity of population and system processes among estuaries and to define the geographical scale over which estuarine research results may be generalized.     

Contribution of the arbuscular mycorrhizal symbiosis to heavy metal phytoremediation

High concentrations of heavy metals (HM) in the soil have detrimental effects on ecosystems and are a risk to human health as they can enter the food chain via agricultural products or contaminated drinking water. Phytoremediation, a sustainable and inexpensive technology based on the removal of pollutants from the environment by plants, is becoming an increasingly important objective in plant research. However, as phytoremediation is a slow process, improvement of efficiency and thus increased stabilization or removal of HMs from soils is an important goal. Arbuscular mycorrhizal (AM) fungi provide an attractive system to advance plant-based environmental clean-up. During symbiotic interaction the hyphal network functionally extends the root system of their hosts. Thus, plants in symbiosis with AM fungi have the potential to take up HM from an enlarged soil volume. In this review, we summarize current knowledge about the contribution of the AM symbiosis to phytoremediation of heavy metals.     

水稻对重金属元素的吸收与分配机理的研究进展

20世纪以来,随着工业的快速发展及人口的大幅度增加,重金属在环境中快速地积累.水稻(Oryza sativa)作为我国最重要的粮食作物,稻田重金属污染不仅导致水稻生长发育受阻,产量下降,更为严重的是重金属在水稻体内大量累积,并通过食物链传递,危害人的健康,直接影响我国的粮食安全.本文就水稻对有毒重金属元素的吸收、运输和分配及其机理方面的最新研究进展进行综述,同时对今后的研究提出看法.     

水稻对重金属元素的吸收与分配机理的研究进展

20世纪以来, 随着工业的快速发展及人口的大幅度增加, 重金属在环境中快速地积累。水稻(Oryza sativa)作为我国最重要的粮食作物, 稻田重金属污染不仅导致水稻生长发育受阻, 产量下降, 更为严重的是重金属在水稻体内大量累积, 并通过食物链传递, 危害人的健康, 直接影响我国的粮食安全。本文就水稻对有毒重金属元素的吸收、运输和分配及其机理方面的最新研究进展进行综述, 同时对今后的研究提出看法。     

水稻对重金属镉的吸收及耐性机理研究进展

Cd是一种不能降解、广泛存在于环境中的金属污染物,是植物体非必需元素、环境中生物毒性最强的重金属元素之一,主要来源于矿山开采、火力发电、机械加工,汽车尾气排放以及磷肥生产等。Cd可通过水稻根部进入机体,向地上部分迁移并蓄积,严重影响水稻正常生长, 并引起稻米Cd污染,通过食物链危害人类健康。从水稻Cd吸收影响因素及Cd在水稻中的吸收、运输和积累机理理等方面对水稻Cd污染研究现状进行综述,系统阐述了土壤pH、Eh、离子浓度等条件对水稻Cd吸收的影响,同时讨论了水稻对Cd胁迫的耐性机理及其分子机制。并指出存在的问题和研究方向。     

Quantitative imaging of metals in tissues

Metals and other trace elements play an important role in many physiological processes in all biological systems. Characterization of precise metal concentrations, their spatial distribution, and chemical speciation in individual cells and cell compartments will provide much needed information to explore the metallome in health and disease. Synchrotron-based X-ray fluorescent microscopy (SXRF) is the ideal tool to quantitatively measure trace elements with high sensitivity at high resolution. SXRF is based on the intrinsic fluorescent properties of each element and is therefore element specific. Recent advances in synchrotron technology and optimization of sample preparation have made it possible to image metals in mammalian tissue with submicron resolution. In combination with correlative methods, SXRF can now, for example, determine the amount and oxidation state of trace elements in intra-cellular compartments and identify cell-specific changes in the metal ion content during development or disease progression.     

Geochemical ecology and problems of health.

The state of health or disease is determined by the nature of the organism, the properties of the biosphere, the heterogeneity of its natural geochemical composition and changes brought about by technology (technogenic changes). For a systematic study of the conditions of health and endemic diseases we have suggested a system of biogeochemical regionalizing of the biosphere with the aid of biospheric taxa: regions of the biosphere, subregions of the biosphere, biogeochemical provinces. The main criteria of the regionalizing are biogenous cycles of chemical elements (links of the biogeochemical food chain from soil-forming rocks to man). An important criterion of the biogeochemical regionalizing is threshold concentrations of chemical elements. The organism regulates its metabolism within the ranges of chemical element concentration between the upper and lower thresholds (necessity range). When chemical elements are present in concentrations above the upper threshold and below the lower threshold, dysfunctions and endemic diseases are observed. Hence, the biogeochemical food chain allows us to establish critical links responsible for the state of health or endemic disease. Principles of optimizing the conditions of the environment and life have been worked out. The creation by us in the U.S.S.R. of biogeochemical maps relating conditions of the environment to biological reactions of organisms has proved a useful method of studying the ecological structure of the biosphere.     

Trace elements in agroecosystems and impacts on the environment.

Trace elements mean elements present at low concentrations (mg kg-1 or less) in agroecosystems. Some trace elements, including copper (Cu), zinc (Zn), manganese (Mn), iron (Fe), molybdenum (Mo), and boron (B) are essential to plant growth and are called micronutrients. Except for B, these elements are also heavy metals, and are toxic to plants at high concentrations. Some trace elements, such as cobalt (Co) and selenium (Se), are not essential to plant growth but are required by animals and human beings. Other trace elements such as cadmium (Cd), lead (Pb), chromium (Cr), nickel (Ni), mercury (Hg), and arsenic (As) have toxic effects on living organisms and are often considered as contaminants. Trace elements in an agroecosystem are either inherited from soil parent materials or inputs through human activities. Soil contamination with heavy metals and toxic elements due to parent materials or point sources often occurs in a limited area and is easy to identify. Repeated use of metal-enriched chemicals, fertilizers, and organic amendments such as sewage sludge as well as wastewater may cause contamination at a large scale. A good example is the increased concentration of Cu and Zn in soils under long-term production of citrus and other fruit crops. Many chemical processes are involved in the transformation of trace elements in soils, but precipitation-dissolution, adsorption-desorption, and complexation are the most important processes controlling bioavailability and mobility of trace elements in soils. Both deficiency and toxicity of trace elements occur in agroecosystems. Application of trace elements in fertilizers is effective in correcting micronutrient deficiencies for crop production, whereas remediation of soils contaminated with metals is still costly and difficult although phytoremediation appears promising as a cost-effective approach. Soil microorganisms are the first living organisms subjected to the impacts of metal contamination. Being responsive and sensitive, changes in microbial biomass, activity, and community structure as a result of increased metal concentration in soil may be used as indicators of soil contamination or soil environmental quality. Future research needs to focus on the balance of trace elements in an agroecosystem, elaboration of soil chemical and biochemical parameters that can be used to diagnose soil contamination with or deficiency in trace elements, and quantification of trace metal transport from an agroecosystem to the environment.     

Influence of Soil Chemistry and Plant Physiology in the Phytoremediation of Cu,Mn, and Zn

Different anthropogenic sources of metals can result from agricultural, industrial, military, mining and urban activities that contribute to environmental pollution. Plants can be grown for phytoremediation to remove or stabilize contaminants in water and soil. Copper (Cu), manganese (Mn) and zinc (Zn) are trace essential metals for plants, although their role in homeostasis in plants must be strictly regulated to avoid toxicity. In this review, we summarize the processes involved in the bioavailability, uptake, transport and storage of Cu, Mn and Zn in plants. The efficiency of phytoremediation depends on several factors including metal bioavailability and plant uptake, translocation and tolerance mechanisms. Soil parameters, such as clay fraction, organic matter content, oxidation state, pH, redox potential, aeration, and the presence of specific organisms, play fundamental roles in the uptake of trace essential metals. Key processes in the metal homeostasis network in plants have been identified. Membrane transporters involved in the acquisition, transport and storage of trace essential metals are reviewed. Recent advances in understanding the biochemical and molecular mechanisms of Cu, Mn and Zn hyperaccumulation are described. The use of plant-bacteria associations, plant-fungi associations and genetic engineering has opened a new range of opportunities to improve the efficiency of phytoremediation. The main directions for future research are proposed from the investigation of published results.     

Relevance of Rhizosphere Research to the Ecological Risk Assessment of Trace Metals in Soils

The chemical, mineralogical, and microbial properties of the rhizosphere of a range of forested ecosystems were studied to identify the key processes controlling the distribution and fate of trace metals at the soil–root interface. The results of our research indicate that: (1) the rhizosphere is a soil microenvironment where properties (e.g., pH, organic matter, microbes) and processes (nutrient and water absorption, exudation) differ markedly from those of the adjacent bulk soil; (2) the rhizosphere is a corrosive medium where the weathering and neoformation of soil solid phases are enhanced; (3) the concentrations of solid-phase and water-soluble trace metals like Cd, Cu, Ni, Pb, and Zn are generally higher in the rhizosphere as shown by both macroscopic and microscopic approaches; (4) a larger fraction of water-soluble metals is complexed by dissolved organic substances in the rhizosphere; and (5) soil microorganisms play, either directly or indirectly, a distinct role on metal speciation, in particular Cu and Zn, in the rhizosphere. These results improve our capacity to estimate metal speciation and bioavailability at the soil–root interface. Furthermore, the research emphasizes the crucial physical position occupied by the rhizosphere with respect to the process of elemental uptake by plants and its key functional role in the transfer of trace metals along the food chain. We conclude that the properties and processes of the rhizosphere should be viewed as key components of assessments of the ecological risks associated with the presence of trace metals in soils.     

Chemical Speciation and Mobility of Some Trace Elements in Vermicomposted Fly Ash

Fly ash, a by-product of power plants, is currently being used extensively in India for soil amendment. However, the toxic elements sorbed in the fly ash might pose a serious threat to the environment, causing soil and water contamination. Vermicomposting of fly ash is expected to reduce the contamination of toxic trace metal and could improve the mobility of essential trace element. The current study is focused on characterizing different species of trace metals and their bio-availability in the vermicomposted fly ash (VCFA)-treated lateritic soil. As a fertilizer, different doses (10%, 20%, 30%, 40%, and 50%) of VCFA were applied to the soil and sequential extraction was carried out to analyze trace elements. In the different fractions, Cr < Mn < Pb < Fe were found to be sorbed more to Fe-Mn oxide-bound fractions, whereas Cd, Cu, and Zn were bound more to organic-matter-bound fractions; Cr and Ni were mostly bound to residual fraction. The Fe-Mn oxides and organic-matter-bound fractions may be bio-available with the appropriate environmental condition, whereas chromium and nickel mostly associated with residual fraction are very difficult to release into the environment. The mobility factor index showed the midlevel substitution (i.e., 10% to 30% of VCFA to lateritic soil) to be beneficial as these doses increased the bio-availability of some essential trace elements and restricted the availability toxic trace metals in the soil. At higher doses, the toxic trace metals were found to be released in the bio-available form, which could be hazardous to the environment.     

Geochemistry and health in the United Kingdom.

Before the 1960s, comparisons between the distribution of trace elements in the environment and health in the United Kingdom were primarily confined to ad hoc studies in areas associated with particular agricultural disorders or with unusual human mortality or morbidity records. More recently, increasing interest in the importance of trace elements in crop and animal production and in the hazards of environmental pollution have created a need for more systematic geochemical data. Geochemical reconnaissance maps for England, Wales, Northern Ireland and parts of Scotland have demonstrated the extent of many known clinical trace element problems in agriculture and have also been valuable in delineating areas within which subclinical disorders may occur. Their application to studies on the composition of soils, food crops and surface waters in relation to public health has proved encouraging. Current knowledge and present investigations into environmental geochemistry and human health in the U.K. are reviewed, together with future research requirements.