The effects of biochar aging on rhizosphere microbial communities in cadmium-contaminated acid soil.

Biochars are widely used in the remediation of Cd-contaminated soils. However, changes in the bacterial communities in the rhizosphere contaminated with Cd in response to biochar aging are poorly studied. Addressing this gap in knowledge is important to improving micro-ecological services on healthy growth of plants with mitigation strategies against Cd contamination. An aging experiment (270 days) was conducted with biochars derived from poultry litter and sugar-gum wood added to a Cd-contaminated acid soil. Bacterial communities in the rhizosphere of Brassica rapa and bulk soils were investigated after 1, 90 and 270 days of biochar aging. There was no significant difference (P > 0.05) in bacterial Shannon and Simpson indices between the control and biochar treatments. However, compared to the no-Cd control, the addition of Cd decreased the relative abundances of Firmicutes, Chloroflexi and Acidobacteriota but increased those of Actinobacteriota and Proteobacteria. Poultry-litter biochar had the largest effect on bacterial community composition, especially in the rhizosphere. Aging of poultry-litter biochar increased the abundance of Armatimonadota over time more than the sugar-gum-wood biochar, which was attributed to a lower pH and higher bioavailability of Cd in the sugar-gum-wood biochar treatment. The addition of poultry-litter biochar to the contaminated soil mitigated the bioaccumulation of Cd by increasing soil pH and restoring soil bacterial ecology in contaminated acid soils over time.

Mechanisms for the removal of Cd(II) and Cu(II) from aqueous solution and mine water by biochars derived from agricultural wastes.

The capacity of biochars derived from agricultural wastes to remove Cd(II) and Cu(II) from aqueous solution and contaminated mine water was evaluated using laboratory-based batch sorption experiments. To examine immobilization of heavy metals, biochars produced in a commercial-scale mobile pyrolizer from feedstocks: poultry litter; lucerne shoot; vetch shoot; canola shoot; wheat straws; and sugar-gum wood, were tested in a liquid-based system. Biochars were characterized by FTIR, XPS and XRD before and after the mine water treatment. Lucerne biochar had the highest Langmuir sorption capacity of Cd(II) (6.28 mg g-1) and vetch-derived biochar had the highest Cu(II) sorption capacity (18.0 mg g-1) at pH 5.5. All the biochars exhibited higher sorption capacity for Cu(II) than for Cd(II). The smaller ionic radius and higher electronegativity of Cu(II), and the PO43-, CO32- and N-containing functional groups of biochars enhanced their binding affinity. The results demonstrated that poultry litter-derived biochar was effective at removal of the Cd(II) and Cu(II) from mine water up to the levels recommended by the World Health Organisation. The results revealed that precipitation with CO32- and PO43-, complexation with -OH and -COOH groups and electrostatic interaction with O-containing surface functional groups were the main mechanisms involved in the removal of multi-metals by biochars, and that selection of feedstock materials for biochar production is important to maximise remediation of multi-metals in contaminated water.

Bovine pancreatic trypsin inhibitor is a new antifungal peptide that inhibits cellular magnesium uptake.

Antimicrobial peptides (AMPs) are promising agents for control of bacterial and fungal infections. Traditionally, AMPs were thought to act through membrane disruption but recent experiments have revealed a diversity of mechanisms. Here we describe a novel antifungal activity for bovine pancreatic trypsin inhibitor (BPTI). BPTI has several features in common with a subset of antimicrobial proteins in that it is small, cationic and stabilized by disulphide bonds. BPTI inhibits growth of Saccharomyces cerevisiae and the human pathogen Candida albicans. Screening of the yeast heterozygous essential deletion collection identified the magnesium transporter Alr1p as a potential BPTI target. BPTI treatment of wild type cells resulted in a lowering of cellular Mg(2+) levels. Populations treated with BPTI had fewer cells in S-phase of the cell cycle and a corresponding increase of cells in G(0)/G(1) and G(2) phases. The same patterns of cell cycle arrest obtained with BPTI were also obtained with the magnesium channel inhibitor hexamine(III)cobalt chloride. Analysis of the growth inhibition of C. albicans revealed that BPTI is inhibiting growth via the same mechanism in the two yeast species. Inhibition of magnesium uptake by BPTI represents a novel mechanism of action for AMPs.