污染控制技术及原理

  • 杨延梅,杨志峰,张相锋,刘鸿亮,席北斗.底物含氮量对厨余堆肥氮素转化及其损失的影响研究[J].环境科学学报,2007,27(6):993-999

  • 底物含氮量对厨余堆肥氮素转化及其损失的影响研究
  • Nitrogen transformation and loss during the composting of food wastes with different nitrogen contents
  • 基金项目:国家高技术研究发展计划(863)项目(No.2001AA644020);国家重点基础研究发展规划(973)项目(No.2005CB724203)
  • 作者
  • 单位
  • 杨延梅
  • 1. 重庆交通大学河海学院, 重庆 400074; 2. 北京师范大学环境学院/环境模拟与污染控制国家重点联合实验室, 北京 100875
  • 杨志峰
  • 北京师范大学环境学院/环境模拟与污染控制国家重点联合实验室, 北京 100875
  • 张相锋
  • 北京师范大学环境学院/环境模拟与污染控制国家重点联合实验室, 北京 100875
  • 刘鸿亮
  • 1. 北京师范大学环境学院/环境模拟与污染控制国家重点联合实验室, 北京 100875; 2. 中国环境科学研究院, 北京 100012
  • 席北斗
  • 中国环境科学研究院, 北京 100012
  • 摘要:采用静态好氧工艺研究了含氮量分别为32.4g·kg-1、45.3g·kg-1和58.2g·kg-1的厨余垃圾(N0、N1、N2)与木屑混合堆制时,堆肥过程中不同形态氮的转化及其氮损失规律.结果表明,堆肥中堆体全氮含量呈先升后降趋势,部分有机氮转化为铵氮导致堆体pH升高,在通风和高温的联合作用下,NH3挥发出堆体造成一定的氮损失.随着底物含氮量的增加,NH3挥发速率和氮损失率均呈上升趋势.堆肥结束时N0、N1、N2的堆体全氮含量分别下降了16.4%、26.3%和21.7%,NH3累计挥发量分别为7.0g·kg-1、9.8g·kg-1和29.4g·kg-1,堆肥氮损失率分别为35·0%、49.9%和53.0%.NH3挥发主要集中在高温阶段的中后期,是厨余堆肥氮损失的主要原因.
  • Abstract:This study investigated nitrogen transformation and loss during the composting of food wastes with added sawdust. Three kinds of food wastes (defined as N0, N1 and N2) were used, containing 32.4g·kg-1, 45.3 g·kg-1 and 58.2 g·kg-1of nitrogen. An aerated static pile compost system was employed to compost the food wastes. The results showed that total nitrogen in the compost first increased and then decreased. Part of the organic nitrogen was transformed into ammonium and which resulted in increased pHof the composting pile. Under the combined effect of high temperature and ventilation, ammonia volatilization from the pile led to nitrogen loss. As the nitrogen content in the food wastes increased, the rate of ammonia emissions and amount of nitrogen loss from the pile was also enhanced. At the end of composting, the accumulated ammonia emissions from all three food wastes, N0,N1 and N2, were 7.0g·kg-1, 9.8 g·kg-1 and 29.4 g·kg-1, respectively. The content of total nitrogen decreased by 16.4%, 26.3% and 21.7%, respectively. The lost amount of nitrogen was 35.0%, 49.9%and 53.0% of the initial total nitrogen amount.Most ammonia volatilization took place in the intermediate and later composting phases at high temperature. Nitrogen losses were attributed mostly to ammonia volatilization.

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