[喀什下游平原区地下水盐渍化特征及成因]。

Han Lu, Yan-Yan Zeng, Jin-Long Zhou, Ying Sun
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引用次数: 0

摘要

本研究揭示了新疆喀什河下游平原区地下水盐渍化分布特征及形成机制,可为当地地下水可持续开发规划提供科学依据,对当地供水安全和社会稳定具有现实意义。2018年9月共采集潜水样15份、浅层承压地下水样38份、深层承压地下水样16份。综合运用数理统计、Duorv图、PCA-APCS-MLR模型、离子比、水文地球化学模拟等方法对样品进行分析。结果表明:地下水总体呈弱碱性(pH值为6.48 ~ 8.60,平均为7.57),总溶解固形物(TDS)为573.0 ~ 16700.0 mg·L-1;地下水主要由Cl-、SO42-、Na+和Ca2+组成。地下水水化学类型主要为HCO3·SO4·Cl、SO4和SO4·Cl。研究区未见卤水,潜水以微咸水和咸水为主,承压地下水以咸水为主。盐渍化系数计算结果表明,从潜水到深部承压地下水,盐渍化程度逐渐增大。蒸发浓度和浸出作用是导致地下水盐渍化的主要因素。碳酸盐岩和硅酸盐岩的溶蚀作用和阳离子交换作用从潜水到深部承压地下水逐渐减弱,而蒸发岩的溶蚀作用始终占主导地位并逐渐加强,这也是造成深部地下水盐度高于浅层地下水的主要因素。农业施肥、地表水灌溉利用不合理、生活污水处理不当等人类活动对地下水盐碱化有一定影响。邻近含水层咸水的渗漏回灌加剧了地下水的盐碱化。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
[Characteristics and Causes of Groundwater Salinization in the Plain Area of the Lower Kashgar River].

This study revealed the distribution characteristics and formation mechanism of groundwater salinization in the plain area of the lower Kashgar River in Xinjiang, which can provide scientific basis for a local sustainable groundwater exploitation plan and practical significance for local water supply security and social stability. Fifteen phreatic water samples, 38 shallow confined groundwater samples, and 16 deep confined groundwater samples were collected in September 2018. Mathematical statistics, a Duorv diagram, PCA-APCS-MLR model, ion ratios, and hydrogeochemical simulations were comprehensively used for sample analysis. The results showed that groundwater was weakly alkaline in general (pH ranged between 6.48 and 8.60 with an average of 7.57), with total dissolved solids (TDS) ranging from 573.0 to 16700.0 mg·L-1. Groundwater was mainly composed of Cl-, SO42-, Na+, and Ca2+. The main groundwater hydrochemical types included were HCO3·SO4·Cl, SO4, and SO4·Cl. No brine was observed in the study area, phreatic water was mainly composed of brackish water and saline water, and confined groundwater was mainly composed of saline water. The salinization coefficient calculation results showed that the salinization degree gradually increased from phreatic water to deep confined groundwater. Evaporation concentration and lixiviation were the main factors leading to the salinization of groundwater. The dissolution and cation exchange of carbonate and silicate rocks gradually weakened from phreatic water to deep confined groundwater, whereas the dissolution of evaporite rock always dominated and was gradually strengthened, which was also the primary factor that caused the salinity of deep groundwater to be higher than that of shallow groundwater. Human activities such as agricultural fertilization, unreasonable use of surface water for irrigation, and improper treatment of domestic sewage had a certain impact on groundwater salinization. The leaking recharge of salt water from adjacent aquifers aggravated the groundwater salinization.

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