首页> 外文学位 >The Performance of Controlled Drainage and inline Denitrifying Woodchip Bioreactor for Reducing Nutrient losses from Subsurface Drained Grassland Receiving Liquid Swine Lagoon Effluent.
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The Performance of Controlled Drainage and inline Denitrifying Woodchip Bioreactor for Reducing Nutrient losses from Subsurface Drained Grassland Receiving Liquid Swine Lagoon Effluent.

机译:受控排水和在线反硝化木片生物反应器降低了接收液态猪泻湖污水的地下排水草地的养分损失的性能。

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摘要

Over application of livestock manure has become a principal nutrient source in groundwater and surface water. Controlled drainage (CD) and denitrifying bioreactors have been used to reduce nutrient losses from artificially drained agricultural land to surface waters. The overall goal of this research was to evaluate the performance of CD and denitrifying woodchip bioreactors for reducing nutrient losses from a subsurface drained grass field receiving liquid swine lagoon effluent (SLE). A four-year field experiment was conducted on a 1.25 ha pasture in eastern North Carolina. Eight subsurface drains (1.0 m depth and 12.5 m spacing), including four experimental drains and four guard drains, were installed in the naturally poorly drained field. Four drains were managed in CD mode with drain outlet set at 36 cm below surface while the remaining four drains were managed in free drainage (FD) mode. Denitrifying bioreactors were installed at the edge of the four experimental drains.;Compared to FD, CD reduced annual subsurface drainage volume by 88% to 98% and raised the mean daily water table by 15 cm. The DRAINMOD model was used to simulate the hydrology of the drained field under both FD and CD scenarios and predict the main components of the water balance. Statistical performance measures indicated acceptable to excellent agreement between predicted and measured water table depth and daily drainage. Results showed clearly that seepage was a significant component of the water balance for the CD plots.;Compared to FD, CD reduced annual load of total nitrogen (TN) in subsurface drainage by 87% to 95%. The estimated population mean (EPM) of nitrate and TN concentrations in drainage water for CD treatment (4.10 and 6.95 mg L-1, respectively) were significantly lower than that from FD treatment (7.52 and 9.06 mg L-1, respectively). The EPM of nitrate concentration in groundwater at three depths (75--225 cm) in CD plots were significantly lower than that from FD plots. Annual load reduction of total phosphorus (TP) through subsurface drain lines in CD treatment ranged from 76% to 95%. The EPM of TP concentration in drainage water for CD plots was 0.18 mg L-1, which was significantly higher than that for FD plots (0.1 mg L-1). The difference of P concentration between CD and FD plots was mainly due to the significant difference of particulate P concentration. Reduced drainage volume, enhanced denitrification, and to a far lesser extent increased grass uptake of N and P during dry growing condition contributed to the observed reduction in N and P loading via subsurface drainage under CD treatment.;All bioreactors significantly reduced nitrate concentrations. Yearly percent nitrate reduction for CD-bioreactor (CDB) and FD-bioreactor (FDB) systems during study period ranged from 48 +/- 22% to 87 +/- 6% and 21 +/- 8% to 51+/- 8%, respectively. Nitrate removal rates increased with water flow rate, initial nitrate concentration, hydraulic retention time (HRT), and temperature; however, the temperature effect was not as strong as the other factors. Longer than needed HRT would also negatively affect nitrate removal rate of bioreactors. Percent nitrate load reduction was affected by the volume of flow that passes through bioreactors rather than bypass pipes. The portion of the water flowing through bioreactors (three out of four) decreased from 2012 to 2014 due to decreasing of estimated saturated hydraulic conductivity of the bioreactor systems. Upflow in-line bioreactors showed sufficient removal of nitrogen loading from drained pasture lands. The practicality of bioreactors was not only related to carbon consumption longevity, but also related to proper maintenance of anaerobic condition, suitable hydraulic conductivity, and appropriate HRT, as well as the management of the whole field drainage system.
机译:过度使用牲畜粪便已成为地下水和地表水的主要营养来源。受控排水(CD)和反硝化生物反应器已被用于减少从人工排水的农田到地表水的养分流失。这项研究的总体目标是评估CD和反硝化木片生物反应器的性能,以减少接收液体猪泻湖污水(SLE)的地下排水草地的营养损失。在北卡罗来纳州东部一个1.25公顷的牧场上进行了为期四年的野外试验。在自然排水不良的地区安装了八个地下排水管(深度为1.0 m,间距为12.5 m),其中包括四个实验排水管和四个防护排水管。四个排水管采用CD模式管理,排水出口设置在地面以下36厘米处,其余四个排水管采用自由排水(FD)模式管理。反硝化生物反应器安装在四个实验排水管的边缘。与FD相比,CD减少了每年的地下排水量,从88%到98%,平均每日地下水位增加了15 cm。 DRAINMOD模型用于模拟FD和CD情况下流失场的水文状况,并预测水平衡的主要组成部分。统计性能指标表明可接受的水位与预测的和测量的水位深度和每日排水量之间的极好的一致性。结果清楚地表明,渗漏是CD积水平衡的重要组成部分;与FD相比,CD减少了地下排水中的总氮(TN)的年负荷,从87%降低到95%。 CD处理的废水中硝酸盐和TN浓度的估计总体平均值(EPM)(分别为4.10和6.95 mg L-1)显着低于FD处理(分别为7.52和9.06 mg L-1)。 CD区中三个深度(75--225 cm)的地下水中硝酸盐浓度的EPM均显着低于FD区。 CD处理中通过地下排水管减少的总磷(TP)的年负荷降低范围为76%至95%。 CD样地的废水中TP的EPM浓度为0.18 mg L-1,显着高于FD样地的EPM(0.1 mg L-1)。 CD和FD图之间P浓度的差异主要是由于颗粒P浓度的显着差异所致。减少的排水量,增强的反硝化作用以及在干燥生长条件下增加的草对N和P的吸收程度要小得多,这有助于在CD处理下通过地下排水观察到N和P负载的减少。所有生物反应器都显着降低了硝酸盐浓度。在研究期间,CD生物反应器(CDB)和FD生物反应器(FDB)系统的硝酸盐年度减少百分比范围为48 +/- 22%至87 +/- 6%和21 +/- 8%至51 +/- 8 %, 分别。硝酸盐去除率随水流量,硝酸盐初始浓度,水力停留时间(HRT)和温度的增加而增加。但是,温度影响不如其他因素强。比所需的HRT长的时间也会对生物反应器的硝酸盐去除率产生负面影响。硝酸盐负荷减少的百分比受通过生物反应器而不是旁通管的流量的影响。从2012年到2014年,流经生物反应器的部分水(四分之三)有所减少,这是由于生物反应器系统的估计饱和水力传导率下降所致。上流式在线生物反应器显示出从流失的牧场中已充分去除了氮负荷。生物反应器的实用性不仅与碳消耗的寿命有关,而且与厌氧条件的适当维持,适当的水力传导率和适当的HRT以及整个田间排水系统的管理有关。

著录项

  • 作者

    Liu, Yu.;

  • 作者单位

    North Carolina State University.;

  • 授予单位 North Carolina State University.;
  • 学科 Agricultural engineering.;Soil sciences.;Engineering.
  • 学位 Ph.D.
  • 年度 2017
  • 页码 338 p.
  • 总页数 338
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

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