660 publications from this institution
In the era of the big data, GIS faces the following challenges and opportunities: the efficient management of very large-scale data, including the data management system and architecture, the real-time processing and analysis of the stream data, and the efficient...
No abstract is provided for this article.
Sulphur fractionation and availability to plants are poorly understood in calcareous soils. Sixty-four calcareous soils containing varying amounts of CaCO3
The ability to locate and quantify elemental distributions in plants is crucial to understanding plant metabolisms, the mechanisms of uptake and transport
No abstract is provided for this article.
Roxarsone [Rox(V)] is widely used as a feed additive in poultry industries. This arsenic-containing compound may be degraded by microbes to release toxic inorganic arsenic in the environment. To date, most of the studies of microbial mediated Rox(V) degradation have focused on anaerobic microorganisms. Here, we isolated a pure cultured aerobic Rox(V)-degrading bacterial strain, CZ-1, from an arsenic-contaminated paddy soil in China. On the basis of 16S rRNA gene sequence, strain CZ-1 was classified as a member of genus Enterobacter. This strain could efficiently degrade Rox(V), converting all of 10 μM Rox(V) within 24 h in liquid culture. Four metabolites including n-acetyl-4-hydroxy-m-arsanilic acid (N-AHPAA[V]), 3-amino-4-hydroxyphenylarsonic acid (3-AHPAA[V]), arsenite (As[III]) and an unknown arsenic compound were detected and identified by HPLC-ICP-MS and HPLC-LC-MS. N-AHPAA(V) was the main product, likely to be formed from acetylation of 3-AHPAA(V). Based on these results, a novel degradation pathway of Rox(V) by Enterobacter. sp CZ-1 is proposed.
Agricultural soils are under threat of toxic metal/metalloid contamination from anthropogenic activities, leading to excessive accumulation of arsenic (As), cadmium (Cd), lead (Pb), and mercury (Hg) in food crops that poses significant risks to human health. Understanding how these toxic metals and their methylated species are taken up, translocated, and detoxified is prerequisite to developing strategies to limit their accumulation for safer food. Toxic metals are taken up and transported across different cellular compartments and plant tissues via various transporters for essential or beneficial nutrients, e.g. As by phosphate and silicon transporters, and Cd by manganese (Mn), zinc (Zn), and iron (Fe) transporters. These transport processes are subjected to interactions with nutrients and the regulation at the transcriptional and post-translational levels. Complexation with thiol-rich compounds, such as phytochelatins, and sequestration in the vacuoles are the common mechanisms for detoxification and for limiting their translocation. A number of genes involved in toxic metal uptake, transport, and detoxification have been identified, offering targets for genetic manipulation via gene editing or transgenic technologies. Natural variations in toxic metal accumulation exist within crop germplasm, and some of the quantitative trait loci underlying these variations have been cloned, paving the way for marker-assisted breeding of low metal accumulation crops. Using plants to extract and remove toxic metals from soil is also possible, but this phytoremediation approach requires metal hyperaccumulation for efficiency. Knowledge gaps and future research needs are also discussed.
Summary The overuse of veterinary antibiotics in animal production and the subsequent land applications of manures contribute to the elevated antibiotic resistance in the soil environment. To minimize the risk of antibiotic resistance, it is important to understand the fate of antibiotics and the spread of antibiotic resistance genes (ARGs) from animal production systems to soil. In this paper, we review recent studies on veterinary antibiotic use, the concentrations of antibiotics and the abundance and diversity of AGRs in animal manures and in soil that receives manures or manure composts. The mechanisms of ARG dissemination in the environment are also discussed. Although we focus on China where around 3 billion tons of animal manures are produced and more than 84 000 tons of antibiotics are consumed annually in animal production industries, the problem is worldwide. Approximately 58% of the veterinary antibiotics consumed are excreted into the environment, more than half of which end up in the soil. The abundance of ARGs in manures can reach up to 10 −1 of the 16S rRNA genes. Applications of manures or manure composts can enrich soil ARGs in at least three ways: (i) by the direct introduction of manure‐derived ARGs, (ii) by elevating the intrinsic soil ARGs and (iii) by imposing a selection of ARGs with the antibiotics in the manures. We also discuss the need for more stringent regulations on the use of veterinary antibiotics and future research directions on the mechanisms of antibiotic resistance and resistance management. Highlights Soil is a natural reservoir of antibiotics and antibiotic resistance genes (ARGs). Manure applications introduce antibiotics and enrich soil ARGs through different mechanisms. Horizontal gene transfer plays an important role in the spread of ARGs from manures. More stringent regulations are needed to reduce the spread of ARG from animal sources.