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冬小麦田O3气孔与非气孔沉降及风险评估
摘要点击 1509  全文点击 475  投稿时间:2017-02-21  修订日期:2017-05-09
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中文关键词  O3干沉降  冬小麦  气孔与非气孔O3沉降通道  产量损失评估
英文关键词  ozone dry deposition  winter wheat  stomatal and non-stomatal pathways  yield risk assessment
作者单位E-mail
徐静馨 南京信息工程大学中国气象局气溶胶与云降水重点开放实验室, 南京 210044 jingxin.xu@mail.utoronto.ca 
郑有飞 南京信息工程大学中国气象局气溶胶与云降水重点开放实验室, 南京 210044
南京信息工程大学江苏省大气环境与装备技术协同创新中心, 南京 210044 
xjx_0718@163.com 
赵辉 南京信息工程大学中国气象局气溶胶与云降水重点开放实验室, 南京 210044  
储仲芳 南京信息工程大学江苏省大气环境与装备技术协同创新中心, 南京 210044  
黄积庆 南京信息工程大学江苏省大气环境与装备技术协同创新中心, 南京 210044  
袁月 南京信息工程大学江苏省大气环境与装备技术协同创新中心, 南京 210044  
中文摘要
      为了深入了解农田生态系统的O3干沉降过程,并基于O3通量(尤其是气孔O3累积通量)指标进行风险评估,利用涡度相关系统对冬小麦田的O3干沉降过程进行了连续动态观测,初步分析O3浓度和总O3通量的变化过程,着重探析气孔O3沉降和非气孔O3沉降的变化特征及其与主要气象因子的关系,并基于剂量指标(AOT40)和通量指标(DFs06)分别推算出冬小麦的产量损失率.结果表明,观测期间(自2016年3月16日至5月30日)日平均O3浓度(cO3)为32.9 nL·L-1;白天(08:00~18:00)和夜间平均总O3通量(FO3)分别为-7.6 nmol·(m2·s)-1和-3.1 nmol·(m2·s)-1,日均FO3为-5.1 nmol·(m2·s)-1.逐日平均气孔O3通量(Fs)的变化范围为0~-5.1 nmol·(m2·s)-1,日均Fs为-1.43 nmol·(m2·s)-1.逐日平均非气孔O3通量(Fns)的变化范围为-1.43~-10.31 nmol·(m2·s)-1,日均Fns为-3.66 nmol·(m2·s)-1.较强的太阳辐射(SR)、较高的温度(T)和适度湿润的条件有利于冬小麦气孔沉降;较强的SR、适度的T和湿润条件是有利于冬小麦非气孔沉降.在整个观测期间,总O3累积吸收通量(DFO3)、气孔O3累积吸收通量(DFs)和非气孔O3累积吸收通量(DFns)分别为31.58、9.99和21.59 mmol·m-2,总DFs和总DFns分别占总DFO3的32%和68%.通过剂量指标AOT40和通量指标DFs06响应方程计算出的冬小麦产量损失率分别为11.58%~20.37%和20%~23.56%.
英文摘要
      To better understand the ozone deposition and risk assessment over agroecosystems based on the ozone flux indices, an eddy-covariance system was used for measuring the ozone deposition continuously and dynamically in a winter wheat field. We analyzed the variations in ozone concentration, total ozone flux, and stomatal and non-stomatal flux. The relationships between stomatal/non-stomatal ozone deposition velocity and the main meteorological factors were investigated. Finally, the yield losses of winter wheat based on the ozone-dose index (AOT40) and ozone flux index (DFs06) were calculated. Results showed that average daily ozone concentration (cO3) was 32.9 nL·L-1. The daytime (08:00-18:00) and nighttime total ozone flux (FO3) were -7.6 nmol·(m2·s)-1 and -3.1 nmol·(m2·s)-1, respectively, and the mean diurnal FO3 was -5.1 nmol·(m2·s)-1. The mean daily stomatal ozone flux (Fs) and non-stomatal ozone flux (Fns) ranged from 0 to -5.1 nmol·(m2·s)-1 and from -1.43 to -10.31 nmol·(m2·s)-1, respectively. The mean diurnal Fs and Fns were -1.43 nmol·(m2·s)-1 and -3.66 nmol·(m2·s)-1. High solar radiation (SR), high temperature (T), and moderate humidity were used to analyze stomatal ozone deposition; high SR, moderate T, and high humidity were suitable to analyze non-stomatal ozone deposition. The cumulative total ozone flux (DFO3), cumulative stomatal ozone flux (DFs), and cumulative non-stomatal ozone flux (DFns) were 31.58, 9.99, and 21.59 mmol·m-2 during the entire experimental period, and DFs and DFns accounted for 32% and 68% of DFO3. The ranges of yield loss in winter wheat were estimated at 11.58%-20.37% and 20%-23.56% using different assessment models based on the ozone dose index AOT40 and ozone flux index DFs06, respectively.

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