Reviews of Environmental Contamination and Toxicology, Vol. by George Ware

By George Ware

Reports of Environmental illness and Toxicology makes an attempt to offer concise, serious experiences of well timed advances, philosophy, and major parts of finished or wanted recreation within the overall box of xenobiotics in any section of our environment, in addition to toxicological implications.

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Soil Biol Biochem 5:249–257. Bartlett RJ (1991) Chromium cycling in soils and water: links, gaps, and methods. Environ Health Perspect 92:17–24. Bartlett RJ, James BR (1979) Behavior of chromium in soils. III. Oxidation. J Environ Qual 8:31–35. Bartlett RJ, Kimble JM (1976) Behavior of chromium in soils. II. Hexavalent forms. J Environ Qual 5:383–386. Basta NT, Gradwohl R (2000) Estimation of Cd, Pb, and Zn bioavailability in smeltercontaminated soils by a sequential extraction procedure. J Soil Contam 9:149–164.

J Soil Sci 36:187–196. Bolan NS, Syers JK, Tillman RW (1986) Ionic strength effects on surface charge and adsorption of phosphate and sulfate by soils. J Soil Sci 37:379–388. Bolan NS, Hedley MJ, White RE (1991) Nitrogen fixation and soil acidification with emphasis on legume based pastures. Plant Soil 134:53–63. Bolan NS, White RE, Hedley MJ (1990) A review of the use of phosphate rock as fertilizer for direct application in Australia and New Zealand. Aust J Exp Agric 30: 297–313. Phosphorus (Im)mobilization of Heavy Metals 37 Bolan NS, Hedley MJ, Loganathan P (1993) Preparation, forms and properties of slowrelease phosphate fertilizers.

25 Reference Bolan et al. (1985) Rajan et al. (1974) Bolan et al. (1986) Sawhney (1974) Schalscha et al. (1974) Naidu et al. (1990) Rajan (1978) Curtin and Syers (1990) Bolan et al. (1999b) obtained a good relationship between the increase in negative charge resulting from H2PO−4 enrichment and the increase in Cd2+ adsorption. However, only a small fraction of the increased negative charge was occupied by Cd2+. In their study, when P was added as KH2PO4, 29% of the increase in negative charge due to H2PO−4 adsorption was evidently balanced by Cd2+ adsorption and the remaining 71% by K+ adsorption.

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