Cadmium biosorption and toxicity to six cadmium-resistant gram-positive bacteria isolated from contaminated soil

Alleviation of salinity and metal stress using plant growth-promoting rhizobacteria isolated from semiarid Moroccan copper-mine soils

Phytoremediation is an eco-friendly method for rehabilitation of mine tailing. Some heavy metals and salt-tolerant plant growth-promoting rhizobacteria (PGPR) could be beneficial in alleviating soil salinity and heavy metal stress during plant growth. The aim of this work is to select PGPR that could be used in phytoremediation process. Twenty-nine rhizobacteria are examined for their ability to grow at increasing concentrations of NaCl, Zn, Pb, Cu, and Cd. The results showed that seventeen rhizobacteria displayed high salinity and metal tolerance up to 100 g L^-1 of NaCl, 5 mM of Cd, 9 mM of Pb, 10 mM of Zn, and 6 mM of Cu. Moreover, almost all tested bacteria maintained their PGP traits under 10% of NaCl and multi-metal stress. Based on seedling bioassay under metallic and salt stress, using Peganum harmala L. and Lactuca sativa L., beneficial effects of seed inoculation with bacterial consortia (Mesorhizobium tamadayense, Enterobacter xiangfangensis, Pseudomonas azotifigens, and Streptomyces caelestis) have been observed in terms of root and shoot elongation. Our results show that the stress-tolerant consortium used has a great potential to sustain plants establishment in heavily disturbed soils.

Comparative study of Cd(II) and Cr(VI) biosorption on Staphylococcus xylosus and Pseudomonas sp. in single and binary mixtures

Biosorption of Cd(II) and Cr(VI) ions in single solutions using Staphylococcus xylosus and Pseudomonas sp., and their selectivity in binary mixtures was investigated. Langmuir and Freundlich models were applied to describe metal biosorption and the influence of pH, biomass concentration and contact time was determined. Maximum uptake capacity of cadmium was estimated to 250 and 278 mg g(-1), whereas that of chromium to 143 and 95 mg g(-1) for S. xylosus and Pseudomonas sp., respectively. In binary mixtures with Cd(II) ions as the dominant species, there is a profound selectivity for cadmium biosorption, reaching 96% and 89% for Pseudomonas sp. and S. xylosus, respectively, at 10 mg l(-1) Cd(II) and 5 mg l(-1) Cr(VI). Interesting, when chromium (VI) ions are the dominant species, there is selectivity towards chromium around 92% with S. xylosus only.

Aflatoxin B1 degradation by flavobacterium aurantiacum in the presence of reducing conditions and seryl and sulfhydryl group inhibitors

This study was undertaken to determine the effects of reducing conditions (L-cysteine) and seryl (phenylmethylsulfonyl fluoride) and sulfhydryl (divalent cadmium) group inhibitors on aflatoxin B1 (AFB1) degradation by Flavobacterium aurantiacum. High-performance liquid chromatography was used to determine AFB1 concentrations in 72-h cultures of F. aurantiacum. The addition of 0.1, 1, or 10 mM L-cysteine did not have any significant effect on AFB1 degradation by these cultures after incubation for 4, 24, or 48 h (P > 0.05). The addition of 0.1 mM phenylmethylsulfonyl fluoride did not significantly decrease AFB1 degradation (P > 0.05), but 1 mM phenylmethylsulfonyl fluoride significantly decreased AFB1 degradation after 4, 24, and 48 h of incubation (P < or = 0.05). No significant difference in AFB1 degradation was obtained with 0.1 mM Cd2+ after 4, 24, or 48 h of incubation (P > 0.05). The addition of 1 and 10 mM Cd2+ significantly decreased AFB1 degradation compared with the cells containing AFB1 alone after 4 and 24 h (P < or = 0.05). The addition of chelators, 1 mM EDTA and 1 mM o-phenanthroline, did not result in removal of inhibition of AFB1 degradation observed with 1 and 10 mM Cd2+. Higher concentration of chelators (>1 mM) are necessary to overcome the inhibitory effect. Further work on the cellular fractions and/or crude enzyme preparations is necessary to determine if indeed sulfhydryl and seryl groups of the enzymes are involved in AFB1 degradation (by maintaining either the structure or function of the enzyme).

The impact of surface attachment on cadmium accumulation by Pseudomonas fluorescens H2

Cadmium accumulation by Pseudomonas fluorescens H2 attached to glass surfaces and by cells free in suspension in maleate buffer was compared and showed several major differences. The time to saturation of cells with Cd(2+) was different for attached and free cells, although both showed biphasic uptake of Cd(2+). The accumulation of Cd(2+) by free cells was inhibited by the presence of zinc but remained several orders of magnitude higher than accumulation by attached cells. The presence of Zn(2+), however, did not inhibit Cd(2+) uptake by cells attached to the solid substratum. Cadmium uptake still increased with Cd(2+) concentration for both free and attached cells in the presence of Zn(2+). The accumulation of Cd(2+) by both free and attached cells increased with pH up to pH 11. The presence of a metabolic inhibitor, carbomyl cyanide m-chlorophenyl-hydrazone, reduced the uptake of Cd(2+) by free cells by 40% but reduced uptake by attached cells by only 25%. Approximately 65% of Cd(2+) accumulated by cells free in suspension was associated with the cell wall, 33% was present in the cytoplasm and only 2% was bound to exopolymer. The results suggest that the characteristics of heavy metal accumulation by bacterial cells are substantially affected by attachment to solid surfaces.

Effect of cadmium and zinc on attachment and detachment interactions of Pseudomonas fluorescens H2 with glass

The physiological and physicochemical bases for the effect of 5, 10, 50, or 100 micrograms of Cd and Zn ml-1 on the attachment and detachment interactions of Pseudomonas fluorescens H2 with glass substrata were determined. Attachment and detachment varied with the type and concentration of metal and the time at which cells were exposed to the metal. The largely inhibitory effect of the metals on bacterial motility and physiological activity did not directly influence attachment. The amount of Cd or Zn accumulated by the cells increased with metal concentration and was greater for free than for attached cells. The hydrophobicity and negative and positive charges of the bacterial surfaces (measured by hydrophobic and electrostatic interaction chromatography) were increased by cell exposure to the metals, particularly after Cd treatment. Cells exposed to Cd prior to attachment showed increased adhesion. Zinc-treated cells did not. There was a positive correlation between adhesion and Cd concentration in the attachment solution. No such relationship existed for Zn. P. fluorescens H2 exposed to Cd prior to attachment desorbed similarly to untreated controls. Zinc pretreatment resulted in decreased desorption. Cells attached in 5 or 10 micrograms of Cd or Zn ml-1 detached less than those attached in 50 or 100 micrograms of Cd or Zn ml-1. The presence of Cd or Zn during detachment had little effect on desorption. The dominant influence of Cd and Zn on attachment and detachment appears to be through modification of the bacterial surface. In natural ecosystems, heavy metals may influence the distribution of bacteria between the solid and liquid phases.