DeVore Cherie L, Hayek Eliane El, Busch Taylor, Long Benson, Mann Michael, Rudgers Jennifer A, Ali Abdul-Mehdi S, Howard Tamara, Spilde Michael N, Brearley Adrian, Ducheneaux Carlyle, Cerrato Josée M
Department of Civil, Construction, Environmental Engineering, University of New Mexico, Albuquerque, New Mexico 87131, United States; Present Address: Department of Earth System Science, Stanford University, Stanford, California 94305, United States.
Department of Chemistry and Chemical Biology, University of New Mexico, Albuquerque, New Mexico 87131, United States; Present Address: Department of Pharmaceutical Sciences, MSC09 5360, University of New Mexico, College of Pharmacy, Albuquerque, New Mexico 87131, United States.
ACS Earth Space Chem. 2021 Jun 17;5(6):1278-1287. doi: 10.1021/acsearthspacechem.0c00302. Epub 2021 Jun 3.
We integrated microscopy, spectroscopy, culturing and molecular biology, and aqueous chemistry techniques to evaluate arsenic (As) accumulation in hydroponically grown inoculated with endophytic fungi. grows in historically contaminated sediment in the Cheyenne River Watershed and was used for laboratory experiments with As(V) ranging from 0 to 2.5 mg L at circumneutral pH. Arsenic accumulation in regional plants has been a community concern for several decades, yet mechanisms affecting As accumulation in plants associated with endophytic fungi remain poorly understood. Colonization of roots by endophytic fungi supported better external and vascular cellular structure, increased biomass production, increased root lengths and increased P uptake, compared to noninoculated plants ( value <0.05). After exposure to As(V), an 80% decrease of As was detected in solution and accumulated mainly in the roots (0.82-13.44 mg kg) of noninoculated plants. Endophytic fungi mediated intracellular uptake into root cells and translocation of As. Electron microprobe X-ray mapping analyses detected Ca-P and Mg-P minerals with As on the root surface of exposed plants, suggesting that these minerals could lead to As adsorption on the root surface through surface complexation or coprecipitation. Our findings provide new insights regarding biological and physical-chemical processes affecting As accumulation in plants for risk assessment applications and bioremediation strategies.
我们整合了显微镜技术、光谱学、培养技术、分子生物学和水相化学技术,以评估接种内生真菌的水培植物中砷(As)的积累情况。[植物名称]生长在夏延河流域历史污染沉积物中,用于在环境中性pH值下进行砷(V)浓度范围为0至2.5mg/L的实验室实验。几十年来,区域植物中的砷积累一直是社区关注的问题,但影响与内生真菌相关的植物中砷积累的机制仍知之甚少。与未接种植物相比,内生真菌对根系的定殖支持了更好的外部和维管细胞结构,增加了生物量生产,增加了根长并增加了磷的吸收(P值<0.05)。暴露于砷(V)后,在溶液中检测到砷减少了80%,且主要积累在未接种植物的根部(0.82 - 13.44mg/kg)。内生真菌介导了砷进入根细胞的细胞内摄取和转运。电子微探针X射线映射分析在暴露植物的根表面检测到含有砷的钙磷和镁磷矿物质,表明这些矿物质可能通过表面络合或共沉淀导致砷吸附在根表面。我们的研究结果为影响植物中砷积累的生物和物理化学过程提供了新的见解,可用于风险评估应用和生物修复策略。