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Toxicity of heavy metals to microorganisms and microbial processes in agricultural soils: a review.

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TLDR
In this article, a hypothesis is formulated to explain how microorganisms may become affected by gradually increasing soil metal concentrations and this is discussed in relation to defining safe or critical soil metal loadings for soil protection.
Abstract
An increasing body of evidence suggests that microorganisms are far more sensitive to heavy metal stress than soil animals or plants growing on the same soils. Not surprisingly, most studies of heavy metal toxicity to soil microorganisms have concentrated on effects where loss of microbial function can be observed and yet such studies may mask underlying effects on biodiversity within microbial populations and communities. The types of evidence which are available for determining critical metal concentrations or loadings for microbial processes and populations in agricultural soil are assessed, particularly in relation to the agricultural use of sewage sludge. Much of the confusion in deriving critical toxic concentrations of heavy metals in soils arises from comparison of experimental results based on short-term laboratory ecotoxicological studies with results from monitoring of long-term exposures of microbial populations to heavy metals in field experiments. The laboratory studies in effect measure responses to immediate, acute toxicity (disturbance) whereas the monitoring of field experiments measures responses to long-term chronic toxicity (stress) which accumulates gradually. Laboratory ecotoxicological studies are the most easily conducted and by far the most numerous, but are difficult to extrapolate meaningfully to toxic effects likely to occur in the field. Using evidence primarily derived from long-term field experiments, a hypothesis is formulated to explain how microorganisms may become affected by gradually increasing soil metal concentrations and this is discussed in relation to defining “safe” or “critical” soil metal loadings for soil protection.

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Journal ArticleDOI

Role of Rhizobacteria in Reduction of Arsenic Uptake by Plants: A Review

TL;DR: In this paper, the identification, characterization and bioremediation advances in effect and significance of As-resistant rhizobacteria in phytoremediations of heavy metal contaminated soils to prevent the transport arsenic metal from root to shoot, and prevent the uptake by plants.
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Copper toxicity in a natural reference soil: ecotoxicological data for the derivation of preliminary soil screening values

TL;DR: The generation of toxicity values for copper (Cu) in a natural reference soil (PTRS1) targeting different terrestrial species, endpoints and soil functions, as to derive a preliminary Cu SSV is aimed at to increase the reliability of the PNEC, and hence of the SSV.
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Phospholipid fatty acid composition of a 2,4,6-trinitrotolune contaminated soil and an uncontaminated soil as affected by a humification remediation process

TL;DR: In this article, the effects of 2,4,6-trinitrotoluene (TNT) contamination and soil remediation on microbial biomass and community structure were investigated.
Journal ArticleDOI

Plant cover and management practices as drivers of soil quality

TL;DR: Soil quality would seem to be strongly affected by the pedogenetic derivation and the management practices more than plant covers, with results highlighted that soils under trees inside the urban park showed higher microbial biomass and activity as compared to soils under grasses.
Journal ArticleDOI

Removal of Cd2+, Zn2+, and Sr2+ by Ion Flotation, Using a Surface-Active Derivative of DTPA (C12-DTPA)

TL;DR: Ion flotation was used for the removal of cadmium, zinc, and strontium ions from aqueous solutions at pH 5-9 in a customized flotation cell, using an aminopolycarboxylic chelating surfactant, 2-dodecyldiethylenetriamine pentaacetic acid (C12-DTPA) in combination with two foaming agents: dodecyltrimethylammonium chloride (DoTAC) and dimethyldodecylylamine-Noxide (D
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Journal ArticleDOI

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