薛文涛, 孙钦平, 林聪, 刘本生, 王悦, 李吉进, 邹国元. 风速对鸡粪沼液氨挥发特性的影响[J]. 农业工程学报, 2018, 34(Z): 7-12. DOI: 10.11975/j.issn.1002-6819.2018.z.002
    引用本文: 薛文涛, 孙钦平, 林聪, 刘本生, 王悦, 李吉进, 邹国元. 风速对鸡粪沼液氨挥发特性的影响[J]. 农业工程学报, 2018, 34(Z): 7-12. DOI: 10.11975/j.issn.1002-6819.2018.z.002
    Xue Wentao, Sun Qinping, Lin Cong, Liu Bensheng, Wang Yue, Li Jijin, Zou Guoyuan. Effect of wind speed on ammonia volatilization characteristics of chicken manure biogas slurry[J]. Transactions of the Chinese Society of Agricultural Engineering (Transactions of the CSAE), 2018, 34(Z): 7-12. DOI: 10.11975/j.issn.1002-6819.2018.z.002
    Citation: Xue Wentao, Sun Qinping, Lin Cong, Liu Bensheng, Wang Yue, Li Jijin, Zou Guoyuan. Effect of wind speed on ammonia volatilization characteristics of chicken manure biogas slurry[J]. Transactions of the Chinese Society of Agricultural Engineering (Transactions of the CSAE), 2018, 34(Z): 7-12. DOI: 10.11975/j.issn.1002-6819.2018.z.002

    风速对鸡粪沼液氨挥发特性的影响

    Effect of wind speed on ammonia volatilization characteristics of chicken manure biogas slurry

    • 摘要: 针对不同风速储存条件沼液氨挥发特性及理化指标变化规律不明晰等问题,设计沼液储存及氨气挥发测定装置,使用强制通风法对氨气取样监测,研究鸡粪沼液在风速0(密闭储存,WS0)、1(气体流量32.33 m3/h,WS1)、2(气体流量65.72 m3/h,WS2)m/s储存条件下的氨挥发特性及总氮(total nitrogen,TN)、化学需氧量(chemical oxygen demand,COD)等降解情况。结果表明,沼液氨挥发通量均呈现先升后降的趋势,均于第12天达到挥发峰值,分别为2.28、4.42和7.21 g/(m2·d),总挥发量分别为1.80、3.90、7.12 g。储存期间沼液温度在13~24 ℃范围波动,总体温度和变化趋势均与室温相似。鸡粪沼液呈现弱碱性,初始pH值为8.38,3组试验在储存过程中pH值均不断上升,试验结束后达到了9.17、8.82、8.92;沼液中氮素主要以铵态氮形式存在,初始铵态氮占总氮含量的84.99%;储存过程中沼液铵态氮质量浓度均呈现先升后降的变化规律,均于第7天达到最高值,分别为3 451.27,3 562.60,3 582.67 mg/L,试验结束后下降到3 030.20、2 762.67、2 794.87 mg/L,降幅为7.64%、15.79%、14.81%。TN和COD降幅均随着风速的增大而增大,TN依次下降了10.97%、18.95%、25.83%;COD依次下降了10.38%、18.61%、20.35%。研究结果可为沼液合理储存以及氨气减排措施的设计提供数据支撑。

       

      Abstract: Abstract: In order to study the characteristics of ammonia (NH3) emission and the variation of its chemical properties under different wind speeds, an equipment for storing biogas slurry and monitoring the NH3 volatilization was designed. Sampling and monitoring of ammonia gas by using forced aeration method, this equipment was used to investigate the NH3 volatilization and degradation of total nitrogen (TN), chemical oxygen demand (COD) of biogas slurry under the wind speeds of 0 (confined storage, WS0), 1 m/s (gas flow 32.33 m3/h, WS1), and 2 m/s (gas flow 65.72 m3/h, WS2). Results showed that the NH3 volatilization of chicken manure biogas slurry showed similar patterns in three wind speed conditions, which increased during the early period followed by decreasing, and all reached their peaks on the 12th day, being of 2.28, 4.42 and 7.21 g/(m2·d), respectively. The total amount of ammonia volatilization during storage is 1.80, 3.90 and 7.12 g, respectively. The temperature of the biogas slurry fluctuated within the range of 13-24 ℃ during the storage, and this temperature fluctuation trend is similar to the changing trend of room temperature for all three conditions. The initial pH value of the chicken manure biogas slurry was 8.38, showing a weak alkalinity. During the storage process, the pH values of WS0, WS1, and WS2 increased continuously, and reached 9.17, 8.82, and 8.92 at the end of storage. The nitrogen element in the chicken manure biogas slurry was mainly kept in the form of ammonium nitrogen, which accounted for 84.99% of the total nitrogen content at the beginning of the test. The concentrations of ammonium nitrogen showed an increasing pattern firstly, and reached their peaks in the seventh day, being of 3 451.27, 3 562.60, and 3 582.67 mg/L, then followed by decreasing, being of 3 030.20, 2 762.67, and 2 794.87 mg/L at the end of the storage. The decline percentages of the ammonium nitrogen were 7.64%, 15.79%, and 14.81% in three conditions, respectively. The declines of TN and COD were positively correlated with the wind speed. The TN content of the biogas slurry decreased by 10.97%, 18.95%, and 25.83%, and the COD concentration decreased by 10.38%, 18.61%, and 20.35%, for WS0, WS1and WS2, correspondingly. Together, these results provide evidence for designing reasonable storage environment of biogas slurry and NH3 mitigation measure.

       

    /

    返回文章
    返回