作物湿地: 一种多功能人工湿地

刘叶叶, 赵亚乾, 沈澄, 卫婷

刘叶叶, 赵亚乾, 沈澄, 卫婷. 作物湿地: 一种多功能人工湿地[J]. 水生生物学报. DOI: 10.7541/2025.2024.0453
引用本文: 刘叶叶, 赵亚乾, 沈澄, 卫婷. 作物湿地: 一种多功能人工湿地[J]. 水生生物学报. DOI: 10.7541/2025.2024.0453
LIU Ye-Ye, ZHAO Ya-Qian, SHEN Cheng, WEI Ting. CROP-WETLAND: A KIND OF CONSTRUCTED WETLAND OWNING MULTI-FUNCTIONS[J]. ACTA HYDROBIOLOGICA SINICA. DOI: 10.7541/2025.2024.0453
Citation: LIU Ye-Ye, ZHAO Ya-Qian, SHEN Cheng, WEI Ting. CROP-WETLAND: A KIND OF CONSTRUCTED WETLAND OWNING MULTI-FUNCTIONS[J]. ACTA HYDROBIOLOGICA SINICA. DOI: 10.7541/2025.2024.0453
刘叶叶, 赵亚乾, 沈澄, 卫婷. 作物湿地: 一种多功能人工湿地[J]. 水生生物学报. CSTR: 32229.14.SSSWXB.2024.0453
引用本文: 刘叶叶, 赵亚乾, 沈澄, 卫婷. 作物湿地: 一种多功能人工湿地[J]. 水生生物学报. CSTR: 32229.14.SSSWXB.2024.0453
LIU Ye-Ye, ZHAO Ya-Qian, SHEN Cheng, WEI Ting. CROP-WETLAND: A KIND OF CONSTRUCTED WETLAND OWNING MULTI-FUNCTIONS[J]. ACTA HYDROBIOLOGICA SINICA. CSTR: 32229.14.SSSWXB.2024.0453
Citation: LIU Ye-Ye, ZHAO Ya-Qian, SHEN Cheng, WEI Ting. CROP-WETLAND: A KIND OF CONSTRUCTED WETLAND OWNING MULTI-FUNCTIONS[J]. ACTA HYDROBIOLOGICA SINICA. CSTR: 32229.14.SSSWXB.2024.0453

作物湿地: 一种多功能人工湿地

基金项目: 国家自然科学基金(42377086和42403056)资助
详细信息
    作者简介:

    刘叶叶(1999—), 女, 硕士研究生; 研究方向为基于人工湿地的水生态修复。E-mail: 1436690411@qq.com

    通信作者:

    赵亚乾, E-mail: yzhao@xaut.edu.cn

  • 中图分类号: X171.5

CROP-WETLAND: A KIND OF CONSTRUCTED WETLAND OWNING MULTI-FUNCTIONS

Funds: Supported by the National Natural Science Foundation of China (42377086 and 42403056)
    Corresponding author:
  • 摘要:

    作物湿地是一种融合人工湿地与农业生产的复合生态系统, 通过充分利用湿地的水文特性和生物净化功能, 在污水处理与作物生长之间实现了优化平衡, 从而缓解传统农业对生态环境的压力, 推动农业与环境的可持续发展。研究系统分析了相关文献, 对作物湿地的植被类型、设计方式及污染物去除效率进行了深入探讨。结果显示, 水稻是作物湿地中最常见的植物, 而湿地类型主要表面流(51.9%)、水平流(33.3%)和浮岛(11.1%)设计, 垂直流的应用较少(3.7%)。作物湿地在水质净化、养分回收、综合农业等方面展现出多重功能, 更适用于低浓度污水的处理, 其处理性能与传统表面流相当。尤其在营养元素回收利用和农业综合发展方面, 作物湿地具有更显著的优势。未来研究应进一步优化作物湿地的设计与管理, 重点关注病原微生物、新污染物和重金属等潜在风险, 确保食品安全和环境健康, 从而更好地实现农业与生态系统的协调发展。

    Abstract:

    Crop wetlands represent an integrated ecological system that combines the principles of constructed wetlands with agricultural production. By leveraging the hydrological characteristics and bioremediation functions of wetlands, crop wetlands achieve an optimized balance between wastewater treatment and crop growth. This approach mitigates the environmental pressures associated with traditional agriculture, thereby promoting sustainable development in agriculture and environmental management. This study systematically analyzed related publications, focusing on vegetation types, wetland configurations, and pollutant removal efficiencies in crop wetlands. The results indicate that paddy field is the most commonly crop wetland while rice is the largely cultivated in such systems. The predominant wetland configuration includes surface flow (51.9%), horizontal flow (33.3%), and floating treatment (11.1%), with vertical flow being less frequently employed (3.7%). Crop wetlands exhibit multiple functionalities, including water quality improvement, nutrient recovery, and integrated agricultural benefits. They are particularly suitable for treating low-concentration wastewater and perform comparably to traditional surface flow constructed wetlands. Notably, crop wetlands demonstrate a significant advantage in nutrient recycling while exhibit the development of integrated agricultural systems. Future research should focus on optimizing the design and management of crop wetlands, with particular emphasis on addressing the potential risks posed by pathogenic microorganisms emerging pollutants and heavy metal. Ensuring food safety and environmental health will be critical to achieving harmonious development between agriculture and ecosystems.

  • 图  1   作物湿地

    a. 植物类型; b. 湿地类型; c. 水质类型

    Figure  1.   Crop wetlands

    a. Plant/crop types; b. Types of wetlands; c. Type of water in crop wetlands

    图  2   稻田和其他作物湿地处理污水浓度

    a. 总氮; b. 总磷

    Figure  2.   Concentration of treated wastewater in paddy and other crop wetlands

    a. total nitrogen; b. total phosphorus

    图  3   稻田和其他作物湿地污水去除效率

    a. 总氮; b. 总磷

    Figure  3.   Wastewater removal efficiency in paddy and other crop wetlands

    a. total nitrogen; b. total phosphorus

    图  4   作物湿地氮磷去除机理及对湿地的影响

    Figure  4.   Nitrogen and phosphorus removal mechanism of crop wetland and its impact on wetland

    表  1   作物湿地的特征及运行效果

    Table  1   Characteristics and operational effects of crop wetlands

    污水类型
    Sewage type
    湿地类型
    Wetland type
    湿地作物
    Wetland crop
    填料
    Substrate
    进水方式
    WFP
    水力停
    留时间
    HRT(d)
    水力负荷
    HLR [m3/(m2·d)]
    湿地面积
    Wetland
    area (m2)
    作物产量
    Crop yield
    (kg/ha)
    进水水质
    TN (%)
    去除率
    TP (%)
    参考文献
    Reference
    Influent quality
    TN (mg/L)
    Removal rate
    TP (mg/L)
    农村生活污水 表面流 水稻 土壤 间歇流 20 9000 8.45 69.30 [8]
    20 8500 2.3 62.90
    20 8300 4.5 66.00
    受污染河水 表面流 饲料水稻 石头、沙子、粉沙、黏土 连续流 0.28 0.20 30 2.53 39.92 [9]
    污水厂尾水 表面流 水稻 土壤 间歇流 13.45 0.72 55.63 86.98 [10]
    农业废水 表面流 黑藻、茭白、荷花、菱角 土壤 间歇流 7—14 2500 4.5 0.13 31.11 22.20 [11]
    农村生活污水 表面流 水稻 土壤 间歇流 20 8648 0.41 65.40 [12]
    间歇流 20 8353 0.21 60.30
    间歇流 20 9324 0.59 71.40
    市政污水 表面流 水稻 土壤 间歇流 25 0.03 1.50 4900 15 2 64.00 40.00 [13]
    0.02 1.50 4700 17.2 3.40 82.60 95.28
    农村生活污水 水平流 香蒲、芦竹、滨海藜 砾石、沙子 连续流 8.00 0.04 5600 22.4 1.70 57.30 76.30 [14]
    农村生活污水 表面流 水稻 土壤 间歇流 20 30.20 65.70 [15]
    20 27.50 71.40
    20 32.70 60.30
    市政污水 表面流 野茭白 土壤 连续流 2-5 0.04 500 20 1.95 48.50 51.30 [16]
    市政污水 表面流 野生稻 土壤 1.95 58.10 64.50 [17]
    受污染河水 表面流 水稻、荷花、金鱼藻 土壤 连续流 2.00 0.09 1,900,000 521.42 0.5 45.61 [18]
    农业废水 表面流 水稻 土壤 间歇流 0.42 0.67 312 9740 1.9 0.17 44.90 43.00 [19]
    农业废水 表面流 海水稻 土壤 间歇流 0.83 0.51 0.76 91.00 [20]
    农村生活污水 表面流 水稻 土壤 间歇式 25 0.02 250 8085 2.1 0.41 [21]
    农村生活污水 潜流 西红柿 砾石、
    沙子
    连续流 1.80 0.22 6.8 7,300 6.7 10.00 [22]
    市政污水 水平流 甘蔗 砖块碎片 连续流 0.99 107000 30 10.6 60.00 77.00 [23]
    甘蔗 碎石灰石 连续流 0.99 67000 30 10.6 58.00 68.00
    市政污水 水平流 甘蔗 建筑骨料、砖块、椰糠 间歇流 2.00 0.05 0.56 20.69 79.93 [24]
    市政污水 水平流 荠菜 砾石、陶粒、黏土 连续流 1.25 0.20 0.75 45 2.03 76.53 79.89 [25]
    芹菜 砾石、陶粒、黏土 连续流 1.25 0.20 0.75 40.345 2.03 71.73 71.95
    水芹 砾石、陶粒、黏土 连续流 1.25 0.20 0.75 43.914 2.03 73.41 80.95
    污水厂
    尾水
    浮岛 韭葱 砾石、
    陶粒
    连续流 1.25 0.20 0.75 30.1 2.86 47.89 [26]
    水平流 茄子 砾石、
    陶粒
    连续流 1.25 0.20 0.75 30.1 2.86 21.47
    浮岛 空心菜 砾石、
    陶粒
    连续流 1.25 0.20 0.75 30.1 2.86 35.38
    水平流 辣椒 砾石、
    陶粒
    连续流 1.25 0.20 0.75 30.1 2.86
    市政污水 浮岛、水平流 黄秋葵 砾石、
    陶粒
    连续流 1.25 0.20 1.50 28.12 2.27 45.10 68.50 [27]
    浮岛、水平流 茄子 砾石、
    陶粒
    连续流 1.25 0.20 1.50 28.12 2.27 33.60 53.60
    浮岛、水平流 辣椒 砾石、
    陶粒
    连续流 1.25 0.20 1.50 28.12 2.27 36.30 59.80
    市政污水 水平流、垂直流 黑麦草 砾石 间歇流 3 0.03 8.48 8 25.80 [28]
    冬小麦 砾石 间歇流 3 0.05 8.48 4 37.90
    农村生活污水 水平流 空心菜 砾石 连续流 3.25 0.30 1.88 14.9 1.10 76.60 78.90 [29]
    农业废水 表面流 水稻 土壤 间歇流 8100 [30]
    注: TN指污水中总氮浓度; TP指污水中总磷浓度; WFP指进水方式; HRT指水力停留时间; HLR指水力负荷; 下同Note: TN refers to the total nitrogen concentration in sewage; TP refers to the total phosphorus; WFP refers to Water flow pattern; HRT refers to hydraulic retention time; HLR refers to the hydraulic loading rate. The same applies below
    下载: 导出CSV

    表  2   作物湿地作物产量

    Table  2   Crop wetlands crop yield

    污水类型
    Sewage type
    湿地类型
    Wetland type
    湿地作物
    Wetland crop
    湿地面积
    Wetland area (m2)
    作物产量
    Crop yield (kg/ha)
    参考文献
    Reference
    农村生活污水黑水表面自由流水稻209000[8]
    灰水水稻208500
    生活废水水稻208300
    地表水水稻208100
    农村生活污水黑水表面自由流水稻208353.3[12]
    灰水水稻209324.3
    生活废水水稻208647.9
    地表水水稻208121.9
    市政污水表面自由流水稻1.54900[13]
    受污染河水表面自由流水稻1900000521.42[18]
    农业废水表面自由流水稻3129740[19]
    农村生活废水表面自由流水稻2508050[21]
    农村生活污水潜流西红柿6.87300[22]
    市政污水水平流甘蔗0.99107000[23]
    甘蔗0.9967000
    下载: 导出CSV
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