Impacts of fluorite dissolution in semiarid endemic soil and ecotoxic effect estimated in Allium cepa.

IF 3.2 3区 环境科学与生态学 Q3 ENGINEERING, ENVIRONMENTAL
Ángel R Díaz-Duarte, Gerardo A Anguiano-Vega, Patricia Ponce-Peña, Roberto Briones-Gallardo, Antonio Aragón-Piña, Ma Guadalupe Nieto-Pescador, Estela Ruiz-Baca, Fabiola S Sosa-Rodríguez, Israel Labastida, René H Lara
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Abstract

Fluorite (CaF2) leaching and weathering (30 days) were conducted to measure fluoride dissolution in semiarid endemic soil and controlled synthetic solutions, and determining the main chemical species involved in these processes via atomic force microscopy (AFM), X-ray diffraction (XRD) and Scanning electron microscopy (SEM-EDS). Ecological health response in this system was assessed exposing Allium cepa bulbs to 10, 50, 100, 450, 550 and 950 mg CaF2 kg-1 soil to determine genotoxic damage, protein and systemic fluorine concentrations. Results indicated 3 cycles of passive-active fluorite dissolution enabling fluoride concentrations up to 164 mg L-1 under endemic conditions; however, highest fluoride dissolution was 780 mg L-1 for synthetic sulfates solution. Cyclic behavior was associated with the formation of ultrafine-sized calcite (CaCO3)-like compounds. Fluorine concentrations ranged from 5 to 300 mg kg-1 in vegetable tissue. The electrophoretic profiles revealed changes in the protein expression after 7, 15 and 25 days of exposure. Genotoxic damage rate was 50, 82 and 42% for these exposures (950 mg CaF2 kg-1 soil). The dose‒response curves of the normalized total protein content revealed the kinetics vegetable health damage rates for only 7 and 25 days. This behavior was best adjusted for only 7 days. These findings exhibited characteristics for initial damage and adaptation-recovery stage after 15 days. Environmental implications of these findings were further discussed.

半干旱地区特有土壤中萤石溶蚀的影响及韭菜的生态毒性效应。
研究了氟石(CaF2)浸出和风化(30 d)对半干旱土质土壤和受控合成溶液中氟化物溶解的影响,并通过原子力显微镜(AFM)、x射线衍射(XRD)和扫描电子显微镜(SEM-EDS)确定了参与这一过程的主要化学物质。采用10、50、100、450、550和950 mg CaF2 kg-1土壤处理大蒜,评价其生态健康反应,测定基因毒性损害、蛋白质和全身氟浓度。结果表明,在地方病条件下,3个被动-主动萤石溶解循环使氟化物浓度达到164 mg L-1;然而,合成硫酸盐溶液的最高氟溶出度为780 mg L-1。循环行为与超细尺寸方解石(CaCO3)类化合物的形成有关。蔬菜组织中的氟浓度为5至300 mg kg-1。电泳图谱显示暴露7、15和25天后蛋白表达的变化。这些暴露(950 mg CaF2 kg-1土壤)的基因毒性损害率分别为50%、82%和42%。标准化总蛋白含量的剂量-响应曲线显示了7天和25天蔬菜健康损害的动力学速率。这种行为最好只调整7天。这些结果显示了15天后的初始损害和适应-恢复阶段的特征。进一步讨论了这些发现对环境的影响。
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来源期刊
Environmental Geochemistry and Health
Environmental Geochemistry and Health 环境科学-工程:环境
CiteScore
8.00
自引率
4.80%
发文量
279
审稿时长
4.2 months
期刊介绍: Environmental Geochemistry and Health publishes original research papers and review papers across the broad field of environmental geochemistry. Environmental geochemistry and health establishes and explains links between the natural or disturbed chemical composition of the earth’s surface and the health of plants, animals and people. Beneficial elements regulate or promote enzymatic and hormonal activity whereas other elements may be toxic. Bedrock geochemistry controls the composition of soil and hence that of water and vegetation. Environmental issues, such as pollution, arising from the extraction and use of mineral resources, are discussed. The effects of contaminants introduced into the earth’s geochemical systems are examined. Geochemical surveys of soil, water and plants show how major and trace elements are distributed geographically. Associated epidemiological studies reveal the possibility of causal links between the natural or disturbed geochemical environment and disease. Experimental research illuminates the nature or consequences of natural or disturbed geochemical processes. The journal particularly welcomes novel research linking environmental geochemistry and health issues on such topics as: heavy metals (including mercury), persistent organic pollutants (POPs), and mixed chemicals emitted through human activities, such as uncontrolled recycling of electronic-waste; waste recycling; surface-atmospheric interaction processes (natural and anthropogenic emissions, vertical transport, deposition, and physical-chemical interaction) of gases and aerosols; phytoremediation/restoration of contaminated sites; food contamination and safety; environmental effects of medicines; effects and toxicity of mixed pollutants; speciation of heavy metals/metalloids; effects of mining; disturbed geochemistry from human behavior, natural or man-made hazards; particle and nanoparticle toxicology; risk and the vulnerability of populations, etc.
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