旱区湿地周边盐渍化农田生态水位阈值与“水位-水量”双控技术

刘鹏飞, 张光辉, 崔尚进, 刘少玉, 聂振龙. 旱区湿地周边盐渍化农田生态水位阈值与“水位-水量”双控技术[J]. 水文地质工程地质, 2022, 49(5): 42-51. doi: 10.16030/j.cnki.issn.1000-3665.202202054
引用本文: 刘鹏飞, 张光辉, 崔尚进, 刘少玉, 聂振龙. 旱区湿地周边盐渍化农田生态水位阈值与“水位-水量”双控技术[J]. 水文地质工程地质, 2022, 49(5): 42-51. doi: 10.16030/j.cnki.issn.1000-3665.202202054
LIU Pengfei, ZHANG Guanghui, CUI Shangjin, LIU Shaoyu, NIE Zhenlong. Threshold value of ecological water table and dual control technology of the water table and its quantity in the salinized farmland around wetland in arid areas[J]. Hydrogeology & Engineering Geology, 2022, 49(5): 42-51. doi: 10.16030/j.cnki.issn.1000-3665.202202054
Citation: LIU Pengfei, ZHANG Guanghui, CUI Shangjin, LIU Shaoyu, NIE Zhenlong. Threshold value of ecological water table and dual control technology of the water table and its quantity in the salinized farmland around wetland in arid areas[J]. Hydrogeology & Engineering Geology, 2022, 49(5): 42-51. doi: 10.16030/j.cnki.issn.1000-3665.202202054

旱区湿地周边盐渍化农田生态水位阈值与“水位-水量”双控技术

  • 基金项目: 国家重点研发计划项目(2017YFC0406100);河北省青年科学基金项目(D2021504040);中国地质调查局基本科研业务费项目(SK202215);中国地质调查局地质调查项目(DD20221752)
详细信息
    作者简介: 刘鹏飞(1986-),男,硕士,助理研究员,主要从事干旱区土壤水盐调控理论与关键技术研究。E-mail:liupengfei0701@163.com
    通讯作者: 张光辉(1959-),男,二级研究员,博士生导师,长期从事水循环演化与水土资源合理开发利用研究。E-mail:Huanjing59@163.com
  • 中图分类号: P641;X173

Threshold value of ecological water table and dual control technology of the water table and its quantity in the salinized farmland around wetland in arid areas

More Information
  • 西北旱区湿地周边农田易盐渍化,合理实时控制和降低地下水水位是实现湿地保护及其周边农田盐渍化防控“双赢”的有效途径。选取西北石羊河流域邓马营湖湿地与农田之间过渡带为示范研究区,通过分析地下水埋深变化特征及其与表层土壤盐分的协同关系,确定生态水位阈值,并基于该阈值研发了由虹吸辐射井群为支撑的地下水“水位-水量”智能双控技术,其关键点是:采用一井虹吸联通多个辐射井,用于增大弱透水层区单井涌水量,实现水位面状控制;利用电系统、信号系统和控制器集成智能控制子系统,实现地下水水位和水量的实时控制。该技术示范应用结果表明:随地下水埋深增大,农田盐渍化风险和湿地植被芦苇覆盖率均降低,农田盐渍化防控和湿地保护的地下水埋深阈值为1.9~3.0 m;每年7—8月的潜水蒸发阶段是表层土壤主要积盐时段,期间智能双控系统可将地下水埋深调控在水位阈限范围;该双控作用不仅能够控降灌溉引起的表层土壤电导率的增大幅度,而且还能有效降低表层土壤的积盐速率;相对微咸水,淡水灌溉条件下智能双控技术的淋盐和控盐效果更明显。因此,这项技术能够实现地下水水位精准调控,对旱区湿地保护及其周边农田盐渍化防控具有重要的现实意义。

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  • 图 1  农田非调控区地下水埋深变化特征(G20监测孔)

    Figure 1. 

    图 2  7月初地下水埋深等值线及监测孔分布位置

    Figure 2. 

    图 3  自然植被区表层土壤盐分与地下水埋深协同变化关系

    Figure 3. 

    图 4  农田区不同潜水埋深下包气带剖面含盐量

    Figure 4. 

    图 5  基于虹吸辐射井群的“水位-水量”双控技术系统

    Figure 5. 

    图 6  示范区功能分区及监测点分布

    Figure 6. 

    图 7  调控区与非调控区地下水埋深动态变化(G06、G20监测孔)

    Figure 7. 

    图 8  灌后8 d地下水埋深等值线

    Figure 8. 

    图 9  调控区淡水(A剖面)、微咸水(B剖面)和非调控区淡水(D剖面)、微咸水(C剖面)灌后相对灌前电导率变幅

    Figure 9. 

    表 1  旱区湿地芦苇适宜生态水位埋深

    Table 1.  Suitable ecological groundwater depth of the wetland bulrush in arid areas

    地区疏勒河流域塔里木河下游黑河流域下游石羊河下游
    水位埋深/m1.0~3.01.0~3.0<3.02.91
    下载: 导出CSV

    表 2  示范区周边不同水位埋深下主要植被类型

    Table 2.  Key vegetational forms in diverse groundwater depths around the demonstration area

    水位埋深/m0.5~2.22.2~3.03.0~5.0
    植被类型芦苇芦苇、盐爪爪盐爪爪、骆驼刺
    下载: 导出CSV

    表 3  主井和辐射井主要参数

    Table 3.  Key parameters of the main pumping and radical wells

    井类型数量/口深度/m井管内径/cm滤水管埋深/m
    主井1850.02~8
    辐射井3631.52~6
    下载: 导出CSV

    表 4  示范区主要监测指标

    Table 4.  Main monitoring indicators in the demonstration zone

    监测对象气象包气带地下水
    监测指标温度、雨量、
    风向、风速等
    温度、含水率和电导率水位、水温和电导率
    监测设备HOBO气象站5TE、MPS-6传感器地下水三参数监测仪
    设备数量1台4组20台
    监测频率每30 min监测1次
    下载: 导出CSV
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出版历程
收稿日期:  2022-02-22
修回日期:  2022-03-18
刊出日期:  2022-09-15

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