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  • 1
    Electronic Resource
    Electronic Resource
    Oxford, UK : Blackwell Science Ltd
    European journal of soil science 54 (2003), S. 0 
    ISSN: 1365-2389
    Source: Blackwell Publishing Journal Backfiles 1879-2005
    Topics: Geosciences , Agriculture, Forestry, Horticulture, Fishery, Domestic Science, Nutrition
    Notes: The behaviour and fate of trace metals, in particular lead and cadmium, when they contaminate the soil as atmospheric fall-out are not well understood. To improve our understanding, we incorporated pure compounds of lead and cadmium into samples taken from surface horizons of three chemically contrasting soils and monitored the changes in their speciation by analysing the soil solution. In most instances the concentrations of trace metals in solution were maximal during the first few days after mixing the contaminants with the soil, and depended strongly on soil type. The exception was when the contaminant was added as sulphide particles. The initial speciation of metals also influenced their solubility, following a decreasing order which did not depend on the soil type:〈displayedItem type="mathematics" xml:id="m1" numbered="no"〉〈mediaResource alt="image" href="urn:x-wiley:13510754:EJSS527:EJSS_527_m1"/〉〈displayedItem type="mathematics" xml:id="m2" numbered="no"〉〈mediaResource alt="image" href="urn:x-wiley:13510754:EJSS527:EJSS_527_m2"/〉Lead sulphide was progressively oxidized, but cadmium sulphide was hardly dissolved. When lead was added as sulphate, between 10 and 20% of lead particles dissolved, regardless of the soil type. For the other species, dissolution was enhanced at lower soil pH. Thermodynamic calculations with the WinHumic V program indicated that the solution was not saturated with respect to lead sulphate. We conclude that dissolution must be limited by the adsorption of inhibitors on reactive surfaces. The calculations also showed that precipitation of chloropyromorphite probably controls lead concentration in leachate from the acid organic soil. Finally, both soil type and initial speciation of contaminants control the behaviour of trace metals in soils for a time greater than a cropping season and must be considered for understanding their environmental impact.
    Type of Medium: Electronic Resource
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  • 2
    ISSN: 0376-6357
    Source: Elsevier Journal Backfiles on ScienceDirect 1907 - 2002
    Topics: Psychology
    Type of Medium: Electronic Resource
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  • 3
    Electronic Resource
    Electronic Resource
    Amsterdam : Elsevier
    Prostaglandins 27 (1984), S. 78 
    ISSN: 0090-6980
    Source: Elsevier Journal Backfiles on ScienceDirect 1907 - 2002
    Topics: Medicine
    Type of Medium: Electronic Resource
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  • 4
    Electronic Resource
    Electronic Resource
    Springer
    Water, air & soil pollution 118 (2000), S. 143-168 
    ISSN: 1573-2932
    Keywords: Cd ; heavy metal ; Pb ; pH ; redox potential ; trace element ; Zn
    Source: Springer Online Journal Archives 1860-2000
    Topics: Energy, Environment Protection, Nuclear Power Engineering
    Notes: Abstract Dissolved trace metals Cd, Pb, Zn, andother solutes were determined after reducingconditions have been imposed to samples of anagricultural polluted soil. The ploughed layer wassampled as undisturbed blocks for floodingexperiments, and sieved samples were incubated inaqueous suspensions at controlled pH (pH 6.2) underdifferent redox conditions. Redox potential and pH,concentrations of major and trace elements, andorganic and inorganic ligands, were measured in thesolutions. Their chemical speciation was calculated byusing the programme Soilchem.These experiments and calculations have shown that pHvariations definitively influence trace metalsolubility, whatever they are induced by reductivedissolution, organic acid formation, or otherprocesses, and that strong acidification can beobtained with well buffered soil when about 1%available carbon is anaerobically transformed intoorganic acids. The organic acids also intervene bycomplexation, particularly for Pb. On another hand,denitrification can limit these effects by consumingprotons and organic substances. Given a steady pH,reducing conditions enhance the mobility of tracemetals, at first by dissolution of manganic and ferricoxides; Pb appeared more sensitive to these processesthan Zn, and finally Cd. As a general rule,hydromorphy in a well-buffered contaminated soil at afirst step should increase the mobility of divalenttrace metals, by decreasing pH and reducing Mn and Feoxides, but prolonged flooding can lead to fix tracemetals again, rather by re-adsorption or precipitationphenomena than by formation of insoluble sulphides.
    Type of Medium: Electronic Resource
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