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吴光伟,李浩林,王庆兵,等. 鲁西北平原地下水高氟与高碘成因分析[J]. 岩矿测试,2023,42(4):793−808. DOI: 10.15898/j.ykcs.202207190134
引用本文: 吴光伟,李浩林,王庆兵,等. 鲁西北平原地下水高氟与高碘成因分析[J]. 岩矿测试,2023,42(4):793−808. DOI: 10.15898/j.ykcs.202207190134
WU Guangwei,LI Haolin,WANG Qingbing,et al. Mobilization Mechanisms of High Fluorine and Iodine Groundwater in the Northwest Shandong Plain[J]. Rock and Mineral Analysis,2023,42(4):793−808. DOI: 10.15898/j.ykcs.202207190134
Citation: WU Guangwei,LI Haolin,WANG Qingbing,et al. Mobilization Mechanisms of High Fluorine and Iodine Groundwater in the Northwest Shandong Plain[J]. Rock and Mineral Analysis,2023,42(4):793−808. DOI: 10.15898/j.ykcs.202207190134

鲁西北平原地下水高氟与高碘成因分析

Mobilization Mechanisms of High Fluorine and Iodine Groundwater in the Northwest Shandong Plain

  • 摘要: 地下水作为鲁西北平原的主要水源,查明高氟、高碘地下水的成因和联系十分必要,可为当地的饮用水安全及解决地方病的研究提供借鉴。目前中国对鲁西北地区浅层高氟地下水的研究较多,但对深层高氟地下水的成因、高氟地下水和高碘地下水的联系有待加强。本文旨在揭示鲁西北平原地下水中氟与碘的空间分布特征,推测高氟地下水的形成机制,查清碘在地下水系统中富集的关键水文地球化学过程,探讨地下水中高氟与高碘的关系。采集浅层(0~55m)、中层(55~225m)、深层(>225m)地下水样品326件,并对18个水化学参数进行层次聚类分析,将地下水样品划分为高氟地下水、高碘地下水和高氟高碘地下水。再结合常规水化学指标和沉积物组分特征进行相关性分析,探讨高氟、高碘地下水的成因及联系。结果表明:高氟地下水与高碘地下水通常伴生出现,且高氟地下水和高碘地下水分布区水化学环境类似,高氟地下水主要集中在地面以下0~40m、50~110m以及225~305m深度内,其最大值(13.71mg/L)出现在地面以下110m深度处;高碘地下水主要集中在地面以下0~10m、55~65m以及225~285m深度内,其最大值(4.601mg/L)出现在234m深度处。含氟矿物萤石(CaF2)的溶解、强烈的蒸发浓缩作用、离子交换可能是高氟地下水的主要形成机制;地下水中的碘主要来自鲁西北平原沉积物中海洋生物和有机质,地下水受强烈的蒸发作用,水走盐留,水中碘浓度不断增加,沉积物淋溶以及氨氮和硫化物的还原溶解可能是导致地下水高碘的主要过程,弱碱性的水环境、还原条件和有机质的存在都是高碘水形成的重要因素。研究区强烈的蒸发浓缩作用、弱碱性的还原条件同时促进了氟和碘的富集。

     

    Abstract:
    BACKGROUND Groundwater is the main water source in the Northwest Shandong Plain Province. It is necessary to find out the causes and connections of high fluorine and high iodine groundwater, which can provide reference for local drinking water safety and solving endemic diseases. At present, there is a lot of research on shallow high fluorine ground water in northwest Shandong, but little research focuses on the cause of deep high fluorine ground water, and the relationship between high fluorine groundwater and high iodine groundwater.
    OBJECTIVES (1) To reveal the spatial distribution characteristics of fluorine and iodine in groundwater in the Northwest Shandong Plain; (2) To speculate the formation mechanism of high fluorine groundwater; (3) To identify the key hydrogeochemical processes of iodine enrichment in the groundwater system; (4) To explore the relationship between high fluorine and high iodine in groundwater.
    METHODS Sediment samples were collected to investigate the lithology, mineral composition and elementary composition of the Northwest Shandong Plain. A total of 326 shallow (0-55m), middle (55-225m) and deep (>225m) groundwater samples were also collected. Hierarchical clustering analysis was applied to classify groundwater based on 18 water chemical parameters (pH, dissolved total solids, sulfate, chlorine, iron, volatile phenols, iodine, fluorine, arsenic, lead, calcium, magnesium, potassium, bicarbonate). The correlation analysis of water chemical parameters and sediment compositions was executed to investigate the causes of high fluorine and iodine groundwater. Furthermore, the calculation of the saturation index of fluorite further helped to determine the main formation mechanism of high fluorine groundwater. The water chemistry type of groundwater was obtained by drawing the piper three-line diagram, and combined with pH and other indicators, the main mechanism of the enrichment of deep high fluorine groundwater was studied. The piper three-line diagram and TDS relationship diagram were drawn to confirm the evaporation concentration mechanism of shallow high iodine groundwater. In addition, the hydrogeological conditions of the study area were analyzed, and the strong reducing environment of deep groundwater in the study area was judged by combining redox environmental sensitive factors, and the main reason for iodine enrichment in deep groundwater was obtained.
    RESULTS The groundwater samples are divided into high fluorine groundwater, high iodine groundwater, and high fluorine and high iodine groundwater by hierarchical clustering analysis. High fluorine groundwater and high iodine groundwater have great similarities, and they are primarily the largest cluster. The high fluorine groundwater is mainly distributed at a depth of 0-40m, 50-110m and 225-305m below the ground surface, with the maximum value (13.7mg/L) occurring at a depth of 110m underground. The high iodine groundwater enriches at 0-10m, 55-65m and 225-285m deep, with the maximum value (4.6mg/L) appearing at 234m underground. Fluorine and iodine in groundwater are often associated, i.e., high fluorine groundwater also has higher iodine content. This is because the enrichment environmental conditions conducive to the two are similar. Strong evaporation concentration and leaching are the main processes leading to high fluorine and high iodine groundwater in the Northwest Shandong Plain. The fluorine-containing minerals and iodine-containing sediments in the shallow groundwater were continuously dissolved, which increased the content of fluorine and iodine in the groundwater. When rainfall occurs, fluorine and iodine in the soil dissolve or leach into the groundwater, resulting in its enrichment. In addition, the alkaline groundwater environment and high HCO3 content can promote the dissolution of fluorine-containing minerals and the enrichment of iodine. The strong reducing groundwater environment and slow flow rate of deep groundwater can be conducive to fluorine enrichment. High fluorine groundwater and high iodine groundwater have similar chemical types, with the main anions of HCO3 and Cl, and the main cation of Na. In a weakly alkaline environment (pH=7-10), high fluorine and high iodine groundwater is formed through leaching and ion exchange.
    CONCLUSIONS The dissolution of fluorine-rich minerals such as fluorite (CaF2), evaporation and ion exchange might be the dominant processes controlling fluorine mobilization in groundwater. The iodine in groundwater mainly comes from marine organisms and organic matter in sediments in the Northwest Shandong Plain. Evaporation, leaching and the reduction dissolution of ammonia nitrogen and sulfide are likely the primary processes leading to iodine enrichment. The weakly alkaline and reducing groundwater environment and the presence of organic matter are all important factors in the formation of high iodine groundwater. Generally, high fluorine groundwater also has high iodine content due to the similar formation mechanisms.

     

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