Sources and distribution of arsenic in agricultural soils of Central Mexico

被引:13
作者
Zanor, Gabriela A. [1 ]
Gabriela Garcia, Maria [2 ]
Eduardo Venegas-Aguilera, Luis [1 ]
Saldana-Robles, Adriana [3 ]
Saldana-Robles, Noe [3 ]
Martinez-Jaime, Oscar A. [4 ]
Segoviano-Garfias, Jose Jesus N. [1 ]
Ramirez-Santoyo, Luis F. [4 ]
机构
[1] Univ Guanajuato, Dept Ciencias Ambientales, Div Ciencias Vida DICIVA, Campus Irapuato Salamanca,Carretera Irapuato, Guanajuato 36500, Mexico
[2] Univ Nacl Cordoba, Ctr Invest Ciencias Tierra, CICTERRA, CONICET, Av Velez Sarsfield 1611,X5016GCA, Cordoba, Argentina
[3] Univ Guanajuato, Dept Ingn Agr, Div Ciencias Vida DICIVA, Campus Irapuato Salamanca,Carretera Irapuato, Guanajuato 36500, Mexico
[4] Univ Guanajuato, Dept Agron, Div Ciencias Vida DICIVA, Campus Irapuato Salamanca,Carretera Irapuato, Guanajuato 36500, Mexico
关键词
As adsorption; As-rich irrigation water; Fe oxides; Entisols; Geoaccumulation index; Vertisols; EL BAJIO GUANAJUATENSE; COMPETITIVE ADSORPTION; WATER; GROUNDWATER; SEDIMENTS; IRON; FLUORIDE; PHOSPHATE; RELEASE; ORIGIN;
D O I
10.1007/s11368-019-02269-8
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
PurposeThe concentrations and distribution of arsenic (As) in two different soil types (Vertisols and Entisols) of Central Mexico impacted by mine activities and irrigation with As-rich groundwater are analyzed in order to determine their impact on the soil quality, and to contribute reliable data that may help to assess the environmental risk that represents the progressive accumulation of As in the arable soils of Guanajuato.Materials and methodsTwo Entisol and two Vertisol profiles located in the Guanajuato state (Mexico) were described and sampled from similar to 1.20-m-deep pits. Soils are irrigated with As-rich deep and shallow groundwaters that were sampled from irrigation boreholes. Additionally, a Vertisol profile located in a parcel not impacted by irrigation was sampled and used as a control soil. Minerals were identified by X-ray diffraction (XRD) and scanning electron microscopy (SEM) coupled with dispersive X-ray spectrometry (EDS). Geoaccumulation indexes (Igeo) were calculated to evaluate As enrichment with respect to a control soil and the Upper Continental Crust (UCC). Anions and cations of groundwater were analyzed by high-performance liquid chromatography (HPLC) and by inductively coupled plasma atomic emission spectroscopy (ICP-AES), respectively. As in soils was determined by ICP-AES.Results and discussionNear total As concentrations are higher in Entisols (mean As value=7.20mg/kg) than in Vertisols (mean As=1.02mg/kg). As concentrations in the control soil are lower (0.34 to 0.70mg/kg). The in-depth distribution of As in Vertisol profiles reveals that the higher As concentrations are found in the uppermost horizons (10cm) and they tend to decrease with depth. In Entisols, As concentrations do not follow a vertical trend. Igeo values of As indicate moderate to heavy As contamination in Vertisols and moderate contamination in Entisols. SEM-EDS analyses revealed the presence of some potential As-bearing minerals such as magnetite and abundant Fe oxides and Ti-Fe coatings precipitated onto feldspar grains, particularly in Entisols.ConclusionsIrrigation of Vertisols with As-rich groundwater determines As concentrations in the uppermost horizons that exceed the natural background of the region (0.4mg/kg). In depth, clay grain-sized particles inhibit the downward migration of As, while Fe oxides and organic matter scavenge As by adsorption. As concentrations in Entisols are higher, and the in-depth distribution of this element is controlled by periodic contributions of As-bearing minerals delivered from mine prospects located at the river's catchments.
引用
收藏
页码:2795 / 2808
页数:14
相关论文
共 49 条
[1]  
Alloway BJ, 2013, HEAVY METALS SOILS T
[2]  
[Anonymous], 2014, KEYS SOIL TAXONOMY
[3]  
[Anonymous], 2000, 6010CSW846 US EPA
[4]  
[Anonymous], 2004, World Health Organization Guidelines for Drinking Water Quality Third Edition, V1
[5]   Arsenic(V) adsorption-desorption in agricultural and mine soils: Effects of organic matter addition and phosphate competition [J].
Arco-Lazaro, Elena ;
Agudo, Ines ;
Clemente, Rafael ;
Pilar Bernal, M. .
ENVIRONMENTAL POLLUTION, 2016, 216 :71-79
[6]   Arsenic and fluoride in the groundwater of Mexico [J].
Armienta, M. A. ;
Segovia, N. .
ENVIRONMENTAL GEOCHEMISTRY AND HEALTH, 2008, 30 (04) :345-353
[7]  
Bundschuh J, 2008, DISTRIBUCION ARSENIC, P33
[8]   Occurrence and treatment of arsenic in groundwater and soil in northern Mexico and southwestern USA [J].
Camacho, Lucy Mar ;
Gutierrez, Wilda ;
Teresa Alarcon-Herrera, Maria ;
de Lourdes Villalba, Maria ;
Deng, Shuguang .
CHEMOSPHERE, 2011, 83 (03) :211-225
[9]  
Chen M, 2002, SOIL SCI SOC AM J, V66, P632, DOI 10.2136/sssaj2002.0632
[10]   The influence of irrigation-induced water table fluctuation on iron redistribution and arsenic immobilization within the unsaturation zone [J].
Chi, Zeyong ;
Xie, Xianjun ;
Pi, Kunfu ;
Wang, Yanxin ;
Li, Junxia ;
Qian, Kun .
SCIENCE OF THE TOTAL ENVIRONMENT, 2018, 637 :191-199