小型农村社区尾水排放通道底泥内源释放特征

彭堰濛, 李云桂, 罗湘, 张志贵, 周远鹏, 孙诗婷. 小型农村社区尾水排放通道底泥内源释放特征[J]. 环境化学, 2020, (5): 1321-1329. doi: 10.7524/j.issn.0254-6108.2019100808
引用本文: 彭堰濛, 李云桂, 罗湘, 张志贵, 周远鹏, 孙诗婷. 小型农村社区尾水排放通道底泥内源释放特征[J]. 环境化学, 2020, (5): 1321-1329. doi: 10.7524/j.issn.0254-6108.2019100808
PENG Yanmeng, LI Yungui, LUO Xiang, ZHANG Zhigui, ZHOU Yuanpeng, SUN Shiting. Characteristics of sediment endogenous release from tailwater discharge channel in small rural communities[J]. Environmental Chemistry, 2020, (5): 1321-1329. doi: 10.7524/j.issn.0254-6108.2019100808
Citation: PENG Yanmeng, LI Yungui, LUO Xiang, ZHANG Zhigui, ZHOU Yuanpeng, SUN Shiting. Characteristics of sediment endogenous release from tailwater discharge channel in small rural communities[J]. Environmental Chemistry, 2020, (5): 1321-1329. doi: 10.7524/j.issn.0254-6108.2019100808

小型农村社区尾水排放通道底泥内源释放特征

    通讯作者: 李云桂, E-mail: liyungui@swust.edu.cn
  • 基金项目:

    四川省科技厅国际合作项目(2017HH0042)资助.

Characteristics of sediment endogenous release from tailwater discharge channel in small rural communities

    Corresponding author: LI Yungui, liyungui@swust.edu.cn
  • Fund Project: Supported by International Cooperation Project of Sichuan Science and Technology Department(2017HH0042).
  • 摘要: 随着农村社区不断聚落化,农村生活污水逐步从分散排放转为中小规模集中排放,研究中小规模农村社区的污水排放特征及环境影响是我国农村水污染控制的重要课题之一.本文选取四川绵阳某小型农村社区为研究对象,监测经简易化粪池集中处理后生活污水的NH3-N和COD排放特征,并采用元素分析和内源静态模拟释放实验研究了该社区排水通道中底泥累积与释放污染物的特性.结果表明,该社区集中排放的生活污水水质较差,致使排水河道严重污染,底泥二次污染风险高.该社区集中排放的生活污水中NH3-N浓度范围为2.9—40.3 mg·L-1;COD浓度范围为33—59 mg·L-1.10年的排放使得社区尾水排放通道底泥污染累积明显,TN含量高达1150—4050 mg·kg-1.底泥内源释放风险不可忽略,主要释放污染物为NH3-N,在UP水中最大释放浓度为3.1 mg·L-1,在上覆水中最大释放浓度为5.9 mg·L-1,均高于GB3838—2002(Ⅴ)类地表水标准.因此,NH3-N应作为农村社区生活污水排放标准中的关键控制指标、也应是分散式生活污水处理设施升级的关键控制指标.低成本NH3-N简易去除装置的研究及推广对降低分散式生活污水排放风险具有重要的意义.
  • 加载中
  • [1] DING R N, LI Y G, YU X, et al. Characteristics of rural agritainment sewage in Sichuan, China[J]. Water Science and Technologyh,2019,79(9):1695-1704.
    [2] CHEN Q W, WANG M, ZHANG J Y, et al. Physiological effects of nitrate, ammonium, and urea on the growth and microcystins contamination of Microcystis aeruginosa:Implication for nitrogen mitigation[J]. Water Research,2019,163:114890.
    [3] MA Y H, ZHAI Y K, ZHENGX Y,et al. Rural domestic wastewater treatment in constructed ditch wetlands:Effects of influent flow ratio distribution[J]. Journal of Cleaner Production,2019,225:350-358.
    [4] YU C Q, HUANG X, CHRN H,et al. Managing nitrogen to restore water quality in China[J]. Nature,2019,567(7749):516-520.
    [5] ZHANG N S, LIU Y S, VAN DEN BRINK P J, et al. Ecological risks of home and personal care products in the riverine environment of a rural region in South China without domestic wastewater treatment facilities[J]. Ecotoxicology and Environmental Safety,2015,122:417-425.
    [6] 王丽丽, 李艳菊, 袁聪颖, 等. 巢湖流域典型村庄生活污水水质年变化特征[J]. 环境化学, 2012,31(7):998-1002.

    WANG L L, LI Y J, YUAN C Y,et al. Temporal change of water quality of the typical rural domestic sewage in Chaohu Lake basin[J].Environmental Chemistry, 2012,31(7):998-1002(in Chinese).

    [7] WANG T, ZHU B, ZHOU M H. Ecological ditch system for nutrient removal of rural domestic sewage in the hilly area of the central Sichuan Basin, China[J]. Journal of Hydrology,2019,570:839-849.
    [8] 马光选. 新农村社区建设:目标与限度[J]. 甘肃行政学院学报, 2009(2):95-101. MA G X. New rural community construction:Objectives and its limits[J]. Journal of Gansu Administrative College,2009

    (2):95-101(in Chinese).

    [9] 闫文秀, 李善峰. 新型农村社区共同体何以可能?——中国农村社区建设十年反思与展望(2006-2016)[J]. 山东社会科学, 2017(12):106-115. YAN W X, LI S F. Why is the new rural community community possible reflections and prospects on the construction of rural communities in China in the past decade (2006

    -2016)[J].Shandong Social Science,2017(12):106-115(in Chinese).

    [10] 郜彗, 金家胜, 李锋, 等. 中国省域农村人居环境建设评价及发展对策[J]. 生态与农村环境学报, 2015,31(6):835-843.

    GAO H, JIN J S, LI F,et al. Evaluation and development strategy of provincial rural human settlement construction in China[J].Journal of Ecology and Rural Environment,2015,31(6):835-843(in Chinese).

    [11] 亓玉军,魏英华,侯述光.农村生活污水治理现状及对策研究[J].环境科学与管理, 2014, 39(6):98-100.

    QI Y J, WEI Y H, HOU S G. Current conditions and countermeasures on treatment of rural domestic sewage[J]. Environmental Science & Management, 2014, 39(6):98-100(in Chinese).

    [12] 陈振华, 侯建辉, 刘津玉. 新型农村社区建设:空间布局与建设模式[J]. 规划师, 2014,30(3):5-12.

    CHEN Z H, HOU J H, LIU J Y. Spatial layout and building model of new rural community[J]. Planners,2014,30(3):5-12(in Chinese).

    [13] ALY N F, BASEM M. Treatment of domestic wastewater using conventional and baffled septic tanks[J]. Environmental Technology,2013,34(13-16):2337.
    [14] 太原工业大学. 室内给水排水工程(第二版)[M]. 北京:中国建筑工业出版社, 1986:121-122. Taiyuan University of Technology. Indoor water supply and drainage (2nd edition)[M]. Beijing:China Building Industry Press, 1986

    :121-122(in Chinese).

    [15] 李新艳,李恒鹏,杨桂山,等.江浙沪地区农村生活污水污染调查[J].生态与农村环境学报,2016,32(6):923-932.

    LI X Y, LI H P, YANG G S, et al. Survey of the Jiangsu, Zhejiang Province and Shanghai Area for rural domestic wastewater pollution[J]. Journal of Ecology and Rural Environment, 2016,32(6):923-932(in Chinese).

    [16] 张丽萍, 袁文权, 张锡辉. 底泥污染物释放动力学研究[J]. 环境污染治理技术与设备, 2003,4(2):22-26.

    ZHANG L P, YUAN W Q, ZHANG X H. Kinetics of pollutants release from sediments[J]. Techniques and Equipment for Environmental Pollution Control,2003,4(2):22-26(in Chinese).

    [17] 梅涵一,王妍,刘云根,等.云南不同类型农村沟渠底泥中氮赋存形态分布[J].环境化学,2016,35(10):2060-2070.

    MEI H Y, WANG Y, LIU Y G, et al. Distribution of nitrogen speciation in ditch sediments from different rural types in Yunnan[J].Environmental Chemistry, 2016,35(10):2060-2070(in Chinese).

    [18] PENG J F, SONG Y H, YUAN P, et al. The remediation of heavy metals contaminated sediment[J]. Journal of Hazardous Materials, 2009, 161(2-3):633-640.
    [19] 袁和忠, 沈吉, 刘恩峰, 等. 太湖水体及表层沉积物磷空间分布特征及差异性分析[J]. 环境科学, 2010,31(4):954-960.

    YUAN H Z, SHEN J, LIU E F, et al. Space distribution characteristics and diversity analysis of phosphorus from overlying water and surface sediments in Taihu Lake[J].Environmental Science, 2010,31(4):954-960(in Chinese).

    [20] ZHANG H X, HUO S L, YEAGER K M, et al. Apparent relationships between anthropogenic factors and climate change indicators and POPs deposition in a lacustrine system[J]. Journal of Environmental Sciences, 2019, 83(9):174-182.
    [21] BellINGER B J, JICHA T M, LEHTO L P, et al. Sediment nitrification and denitrification in a Lake Superior estuary[J]. Journal of Great Lakes Research,2014,40(2):392-403.
    [22] CHEN L M, LIU S T, CHEN Q, et al. Anammox response to natural and anthropogenic impacts over the Yangtze River[J]. Science of the Total Environment,2019,665:171-180.
    [23] 廖日红, 顾华, 申颖洁, 等. 北京市农村生活污水排放现状调研与分析[J].中国给水排水,2011,27(2):30-33.

    LIAO R H, GU H, SHEN Y J, et al. Investigation and analysis of rural domestic sewage discharge situation in Beijing Suburbs[J]. China Water & Wastewater, 2011,27(2):30-33(in Chinese).

    [24] 凌霄, 杨细平, 陈满, 等. 广东省农村生活污水治理现状调查[J]. 中国给水排水, 2009,25(8):8-10

    ,15. LING X, YANG X P, CHEN M, et al. Investigation on present situation of rural domestic sewage treatment in Guangdong Province[J].China Water & Wastewater, 2009,25(8):8-10,15(in Chinese).

    [25] 陈穗玲, 李锦文, 崔明超, 等. 广州大学城某校园地表水"三氮"浓度的时间变化特征及自净状态分析[J]. 环境化学, 2013,32(4):704-705.

    CHEN H L, LI J W, CUI M C, et al. Time variation characteristics and self-purification status analysis of "Three Nitrogen" concentration in surface water of a campus in Guangzhou university town[J].Environmental Chemistry, 2013,32(4):704-705(in Chinese).

    [26] 任爽, 吴壤.水体自净过程中不同污染物降解速率常数的相性研究[J].环境与发展,2018,30(09):102-104.

    REN S, WU R. Study on phase characterization of different pollutant degradation rate constants in self-cleaning process of water body[J].Inner Mongolia Environmental Sciences, 2018,30(09):102-104(in Chinese).

    [27] 杨枫,王圣瑞,郭伟, 等.滇池入湖污水处理厂尾水COD降解过程及光谱特征[J]. 环境工程技术学报,2017,7(5):558-564.

    YANG F, WANG S R, GUO W, et al. Spectroscopic analysis and degradation kinetics study of COD in sewage plant effluent into Dianchi Lake[J].Journal of Environmental Engineering Technology, 2017,7(5):558-564(in Chinese).

    [28] 郭加汛, 彭俊翔, 张海涛, 等.太湖流域典型河流含氮物消减速率研究[J]. 中国环境科学, 2016,36(10):3026-3032.

    GUO J X, PENG J X, ZHANG H T, et al. Study on reduction rates of nitrogen pollution in typical rivers of Taihu Basin[J].China Environmental Science, 2016,36(10):3026-3032(in Chinese).

    [29] MARTINOVA M V. Nitrogen and phosphor compounds in bottom sediments:Mechanisms of accumulation, transformation and release[J]. Hydrobiologia, 1993, 252(1):1-22.
    [30] HILDA D M, MARÍN JULIO, ELIZABETH G, et al. Nitrogen mobility at the sediment-water interface of Lake Maracaibo, Venezuela[J]. Water Air & Soil Pollution, 2003, 145(1-4):341-357.
    [31] WANG S, JIN X, NIU D, et al. Potentially mineralizable nitrogen in sediments of the shallow lakes in the middle and lower reaches of the Yangtze River area in China[J]. Water & Environment Journal, 2009, 24(9):1788-1792.
    [32] 莫祖澜, 邵卫云, 刘小为.自然与引水因素对受纳水体自净作用的影响研究[J]. 科技通报, 2014,30(9):202-207

    ,229. WU Z L, SHAO W Y, LIU X W. Effects of natural and water diversion factors on self-purification of the receiving waters[J]. Bulletin of Science and Technology, 2014,30(9):202-207,229(in Chinese).

    [33] 吴群河, 曾学云, 黄钥.河流底泥中DO和有机质对三氮释放的影响[J]. 环境科学研究, 2005,18(5):34-39.

    WU Q H, ZENG X Y, HUANG Y. Influence of DO and organic matter on nitrogen (NH4+-N, NO2--N and NO3--N) releasing in the sediment of river[J]. Research of Environmental Sciences, 2005,18(5):34-39(in Chinese).

  • 加载中
计量
  • 文章访问数:  1588
  • HTML全文浏览数:  1588
  • PDF下载数:  36
  • 施引文献:  0
出版历程
  • 收稿日期:  2019-10-08

小型农村社区尾水排放通道底泥内源释放特征

    通讯作者: 李云桂, E-mail: liyungui@swust.edu.cn
  • 1. 西南科技大学环境与资源学院环境工程系, 绵阳, 621010;
  • 2. 低成本废水处理技术四川省国际科技合作基地, 绵阳, 621010
基金项目:

四川省科技厅国际合作项目(2017HH0042)资助.

摘要: 随着农村社区不断聚落化,农村生活污水逐步从分散排放转为中小规模集中排放,研究中小规模农村社区的污水排放特征及环境影响是我国农村水污染控制的重要课题之一.本文选取四川绵阳某小型农村社区为研究对象,监测经简易化粪池集中处理后生活污水的NH3-N和COD排放特征,并采用元素分析和内源静态模拟释放实验研究了该社区排水通道中底泥累积与释放污染物的特性.结果表明,该社区集中排放的生活污水水质较差,致使排水河道严重污染,底泥二次污染风险高.该社区集中排放的生活污水中NH3-N浓度范围为2.9—40.3 mg·L-1;COD浓度范围为33—59 mg·L-1.10年的排放使得社区尾水排放通道底泥污染累积明显,TN含量高达1150—4050 mg·kg-1.底泥内源释放风险不可忽略,主要释放污染物为NH3-N,在UP水中最大释放浓度为3.1 mg·L-1,在上覆水中最大释放浓度为5.9 mg·L-1,均高于GB3838—2002(Ⅴ)类地表水标准.因此,NH3-N应作为农村社区生活污水排放标准中的关键控制指标、也应是分散式生活污水处理设施升级的关键控制指标.低成本NH3-N简易去除装置的研究及推广对降低分散式生活污水排放风险具有重要的意义.

English Abstract

参考文献 (33)

目录

/

返回文章
返回