Ying He, Boqiang Fan, Mengqi Li, Zhang Yujun, Kun You, Hao Xie, Dongqi Yu, Boen Lei, Li Xiaoyi, Jian-guo Liu, Wenqing Liu
{"title":"CO2和NH3区域发射激光吸收光谱检测技术研究","authors":"Ying He, Boqiang Fan, Mengqi Li, Zhang Yujun, Kun You, Hao Xie, Dongqi Yu, Boen Lei, Li Xiaoyi, Jian-guo Liu, Wenqing Liu","doi":"10.12783/dteees/peems2019/34004","DOIUrl":null,"url":null,"abstract":"High-sensitivity emission monitoring of CO2 and NH3 in farmland region is very important for analyzing environment and climate change. The on-line detection technology was studied based on open-path tunable diode laser absorption spectroscopy technology (OP-TDLAS). The detection spectrum of open path was extracted to realize accurate concentration inversion by designing the multi-line fitting algorithm. The system detection stability was evaluated by Allan variance that the detection limit of NH3 and CO2 were about 0.048 L/L and 4.31 L/L respectively. The detection experiment was carried out in farmland of north Anhui to prove that both of the fertilization and straw returning to the field were the emission source of CO2 and NH3 from soil. The growth effect of the former was slower but higher than that of fertilization. This stable spectrum detection method can obtain large-scale concentration results and clear emission rules, which provide technical support for the environment-friendly agriculture. Introduction In recent years, our country has adopted straw returning to the field [1,2] which has changed the physical and chemical properties of the soil in a certain extent and even increased the possibility of CO2 and NH3 emission from the soil. Therefore, CO2 and NH3 emission data in large-scale farmland need obtain by effective and stable detection method to assess its impact on the atmospheric environment, which has become an urgent problem in agriculture and environmental fields [3,4] . Gas monitoring in farmland ecosystem usually adopts box method [5] , micrometeorology method [6-7] and so on. These methods mainly study local soil emissions which are vulnerable to environmental factors, and the requirements to underlying surface and atmospheric stability are high. In recent years, open-path tunable diode laser absorption spectroscopy (OP-TDLAS) technology has been gradually applied for large-scale monitoring. This technology [8,9] continuously measures the gas without sampling and pretreatment. It is more effective to monitor adsorbed gases (such as NH3). Moreover, it has the advantage of fast detection [10] and high sensitivity combined with long optical path technology. Flesch et al. (2007) measured methane volatilization in pasture based on TDLAS technology to verify its measurement accuracy. Todd et al. (2015) carried out ammonia emission monitoring in dairy farmland, and the volatilization rate obtained was 304g·head -1 ·d -1 . Anning Zhu et al. (2012) carried out ammonia emission monitoring before and after nitrogen fertilizer application in Huang-Huai-Hai farmland with TDLAS and BLS technology to obtain the emission rule. At present, there are few reports on effective extraction of characteristic absorption spectrum and improvement of detection stability in open-path detection. In this paper, the multi-line fitting algorithm was designed to realize spectrum detection. Allan variance analysis was carried out to determine the measurement stability, and the OP-TDLAS system was used to monitor CO2 and NH3 regional Emission in farmland. Basic Principles According to Lambert-Beer's law, the monochromatic laser with the laser emitting frequency and initial light intensity 0 I passes through an absorption medium with certain length of L, and the relationship between laser received intensity t I and absorbance A is expressed as: 0 ln t I k L A I (1) k is the spectral absorption coefficient of a single gas at a single transition: kv=S(T) ( ) v Px (2) where S(T) is the line strength, P is the pressure, x is the gas concentration, ( ) v is a normalized linear function. By integrating formula (2), the gas concentration is expressed as [11] : ( ) A x S T PL (3) The wavelength range of spectral transition was tuned to retrieve the gas concentration from the transition absorbance results when the temperature, line strength and pressure are known. Detection System and Technology System Design The OP-TDLAS system structure is shown in Fig. 1. The DFB lasers are used as light sources to monitor NH3 absorption line at 6528.8cm −1 and CO2 absorption line at 6336.3cm −1 respectively. The beam combiner couples the two time-division scanned laser beams and divided them into three beams. One beam passed a reference cell filled with standard gases, and the other two beams transmitted to the open optical system consisting of the telescope and retro-reflector. The two optical systems used to measure respectively the gases absorption spectrum of background path and downwind path for quantitatively inverting the concentration. Temperatur e controller Current supply Signal processing module Detector1 Detector3 NH3 DFB laser Beam splitter Collimator Measurement open path Reference path Data acquisition processor DAC","PeriodicalId":11369,"journal":{"name":"DEStech Transactions on Environment, Energy and Earth Science","volume":"182 1","pages":""},"PeriodicalIF":0.0000,"publicationDate":"2020-04-01","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"1","resultStr":"{\"title\":\"Research on Laser Absorption Spectrum Detection Technology for CO2 and NH3 Regional Emission\",\"authors\":\"Ying He, Boqiang Fan, Mengqi Li, Zhang Yujun, Kun You, Hao Xie, Dongqi Yu, Boen Lei, Li Xiaoyi, Jian-guo Liu, Wenqing Liu\",\"doi\":\"10.12783/dteees/peems2019/34004\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"High-sensitivity emission monitoring of CO2 and NH3 in farmland region is very important for analyzing environment and climate change. The on-line detection technology was studied based on open-path tunable diode laser absorption spectroscopy technology (OP-TDLAS). The detection spectrum of open path was extracted to realize accurate concentration inversion by designing the multi-line fitting algorithm. The system detection stability was evaluated by Allan variance that the detection limit of NH3 and CO2 were about 0.048 L/L and 4.31 L/L respectively. The detection experiment was carried out in farmland of north Anhui to prove that both of the fertilization and straw returning to the field were the emission source of CO2 and NH3 from soil. The growth effect of the former was slower but higher than that of fertilization. This stable spectrum detection method can obtain large-scale concentration results and clear emission rules, which provide technical support for the environment-friendly agriculture. Introduction In recent years, our country has adopted straw returning to the field [1,2] which has changed the physical and chemical properties of the soil in a certain extent and even increased the possibility of CO2 and NH3 emission from the soil. Therefore, CO2 and NH3 emission data in large-scale farmland need obtain by effective and stable detection method to assess its impact on the atmospheric environment, which has become an urgent problem in agriculture and environmental fields [3,4] . Gas monitoring in farmland ecosystem usually adopts box method [5] , micrometeorology method [6-7] and so on. These methods mainly study local soil emissions which are vulnerable to environmental factors, and the requirements to underlying surface and atmospheric stability are high. In recent years, open-path tunable diode laser absorption spectroscopy (OP-TDLAS) technology has been gradually applied for large-scale monitoring. This technology [8,9] continuously measures the gas without sampling and pretreatment. It is more effective to monitor adsorbed gases (such as NH3). Moreover, it has the advantage of fast detection [10] and high sensitivity combined with long optical path technology. Flesch et al. (2007) measured methane volatilization in pasture based on TDLAS technology to verify its measurement accuracy. Todd et al. (2015) carried out ammonia emission monitoring in dairy farmland, and the volatilization rate obtained was 304g·head -1 ·d -1 . Anning Zhu et al. (2012) carried out ammonia emission monitoring before and after nitrogen fertilizer application in Huang-Huai-Hai farmland with TDLAS and BLS technology to obtain the emission rule. At present, there are few reports on effective extraction of characteristic absorption spectrum and improvement of detection stability in open-path detection. In this paper, the multi-line fitting algorithm was designed to realize spectrum detection. Allan variance analysis was carried out to determine the measurement stability, and the OP-TDLAS system was used to monitor CO2 and NH3 regional Emission in farmland. Basic Principles According to Lambert-Beer's law, the monochromatic laser with the laser emitting frequency and initial light intensity 0 I passes through an absorption medium with certain length of L, and the relationship between laser received intensity t I and absorbance A is expressed as: 0 ln t I k L A I (1) k is the spectral absorption coefficient of a single gas at a single transition: kv=S(T) ( ) v Px (2) where S(T) is the line strength, P is the pressure, x is the gas concentration, ( ) v is a normalized linear function. By integrating formula (2), the gas concentration is expressed as [11] : ( ) A x S T PL (3) The wavelength range of spectral transition was tuned to retrieve the gas concentration from the transition absorbance results when the temperature, line strength and pressure are known. Detection System and Technology System Design The OP-TDLAS system structure is shown in Fig. 1. The DFB lasers are used as light sources to monitor NH3 absorption line at 6528.8cm −1 and CO2 absorption line at 6336.3cm −1 respectively. The beam combiner couples the two time-division scanned laser beams and divided them into three beams. One beam passed a reference cell filled with standard gases, and the other two beams transmitted to the open optical system consisting of the telescope and retro-reflector. The two optical systems used to measure respectively the gases absorption spectrum of background path and downwind path for quantitatively inverting the concentration. 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引用次数: 1
摘要
农田CO2和NH3的高灵敏度排放监测对分析环境和气候变化具有重要意义。研究了基于开路可调谐二极管激光吸收光谱技术(OP-TDLAS)的在线检测技术。通过设计多线拟合算法,提取开路检测谱,实现浓度精确反演。通过Allan方差评价体系的检测稳定性,NH3和CO2的检出限分别为0.048L/L和4.31L/L。在皖北农田进行了检测试验,证明施肥和秸秆还田都是土壤CO2和NH3的排放源。前者的生长效果较施肥慢,但高于施肥。这种稳定的光谱检测方法可以获得大规模的浓度结果和清晰的排放规律,为环境友好型农业提供技术支持。近年来,我国采用秸秆还田[1,2],在一定程度上改变了土壤的理化性质,甚至增加了土壤排放CO2和NH3的可能性。因此,需要通过有效、稳定的检测方法获取大规模农田CO2和NH3排放数据,评估其对大气环境的影响,这已成为农业和环境领域亟待解决的问题[3,4]。农田生态系统气体监测通常采用箱法[5]、微气象法[6-7]等。这些方法主要研究易受环境因素影响的局部土壤排放,对下垫面和大气稳定性要求较高。近年来,开路可调谐二极管激光吸收光谱(OP-TDLAS)技术已逐渐应用于大规模监测。该技术[8,9]无需采样和预处理即可连续测量气体。对吸附气体(如NH3)的监测更有效。并且结合长光路技术具有检测速度快[10]、灵敏度高的优点。Flesch et al.(2007)基于TDLAS技术对牧场甲烷挥发进行了测量,验证了其测量精度。Todd等(2015)对奶牛场进行了氨排放监测,得到的挥发率为304g·head -1·d -1。朱安宁等(2012)利用TDLAS和BLS技术对黄淮海农田施氮前后的氨排放进行了监测,得到了排放规律。目前,开路检测中有效提取特征吸收光谱和提高检测稳定性的报道很少。本文设计了多线拟合算法来实现频谱检测。采用Allan方差分析确定测量结果的稳定性,并采用OP-TDLAS系统对农田CO2和NH3区域排放进行监测。基本原则根据Lambert-Beer定律,单色激光的激光发射频率和初始光强度0我穿过一个吸收介质有一定的长度L和激光接收之间的关系强度t我和吸光度表示为:0 ln t我k L(1)k单一气体的光谱吸收系数在一个转变:kv=S(T) () v Px(2)其中S(T)为线强度,P为压力,x为气体浓度,()v为归一化线性函数。通过对式(2)积分,气体浓度表示为[11]:()A x S T PL(3)在温度、谱线强度和压力已知的情况下,调整光谱跃迁波长范围,从跃迁吸光度结果中提取气体浓度。探测系统与技术系统设计OP-TDLAS系统结构如图1所示。采用DFB激光器作为光源,分别监测了6528.8cm−1的NH3吸收线和6336.3cm−1的CO2吸收线。光束合并器将两束时分扫描激光束耦合,并将其分成三束。一束光通过一个充满标准气体的基准室,另外两束光进入由望远镜和反光镜组成的开放式光学系统。两种光学系统分别用于测量背景路径和顺风路径的气体吸收光谱,用于定量反演浓度。温度控制器电流供应信号处理模块Detector1 Detector3 NH3 DFB激光分束器准直器测量开路参考路径数据采集处理器DAC
Research on Laser Absorption Spectrum Detection Technology for CO2 and NH3 Regional Emission
High-sensitivity emission monitoring of CO2 and NH3 in farmland region is very important for analyzing environment and climate change. The on-line detection technology was studied based on open-path tunable diode laser absorption spectroscopy technology (OP-TDLAS). The detection spectrum of open path was extracted to realize accurate concentration inversion by designing the multi-line fitting algorithm. The system detection stability was evaluated by Allan variance that the detection limit of NH3 and CO2 were about 0.048 L/L and 4.31 L/L respectively. The detection experiment was carried out in farmland of north Anhui to prove that both of the fertilization and straw returning to the field were the emission source of CO2 and NH3 from soil. The growth effect of the former was slower but higher than that of fertilization. This stable spectrum detection method can obtain large-scale concentration results and clear emission rules, which provide technical support for the environment-friendly agriculture. Introduction In recent years, our country has adopted straw returning to the field [1,2] which has changed the physical and chemical properties of the soil in a certain extent and even increased the possibility of CO2 and NH3 emission from the soil. Therefore, CO2 and NH3 emission data in large-scale farmland need obtain by effective and stable detection method to assess its impact on the atmospheric environment, which has become an urgent problem in agriculture and environmental fields [3,4] . Gas monitoring in farmland ecosystem usually adopts box method [5] , micrometeorology method [6-7] and so on. These methods mainly study local soil emissions which are vulnerable to environmental factors, and the requirements to underlying surface and atmospheric stability are high. In recent years, open-path tunable diode laser absorption spectroscopy (OP-TDLAS) technology has been gradually applied for large-scale monitoring. This technology [8,9] continuously measures the gas without sampling and pretreatment. It is more effective to monitor adsorbed gases (such as NH3). Moreover, it has the advantage of fast detection [10] and high sensitivity combined with long optical path technology. Flesch et al. (2007) measured methane volatilization in pasture based on TDLAS technology to verify its measurement accuracy. Todd et al. (2015) carried out ammonia emission monitoring in dairy farmland, and the volatilization rate obtained was 304g·head -1 ·d -1 . Anning Zhu et al. (2012) carried out ammonia emission monitoring before and after nitrogen fertilizer application in Huang-Huai-Hai farmland with TDLAS and BLS technology to obtain the emission rule. At present, there are few reports on effective extraction of characteristic absorption spectrum and improvement of detection stability in open-path detection. In this paper, the multi-line fitting algorithm was designed to realize spectrum detection. Allan variance analysis was carried out to determine the measurement stability, and the OP-TDLAS system was used to monitor CO2 and NH3 regional Emission in farmland. Basic Principles According to Lambert-Beer's law, the monochromatic laser with the laser emitting frequency and initial light intensity 0 I passes through an absorption medium with certain length of L, and the relationship between laser received intensity t I and absorbance A is expressed as: 0 ln t I k L A I (1) k is the spectral absorption coefficient of a single gas at a single transition: kv=S(T) ( ) v Px (2) where S(T) is the line strength, P is the pressure, x is the gas concentration, ( ) v is a normalized linear function. By integrating formula (2), the gas concentration is expressed as [11] : ( ) A x S T PL (3) The wavelength range of spectral transition was tuned to retrieve the gas concentration from the transition absorbance results when the temperature, line strength and pressure are known. Detection System and Technology System Design The OP-TDLAS system structure is shown in Fig. 1. The DFB lasers are used as light sources to monitor NH3 absorption line at 6528.8cm −1 and CO2 absorption line at 6336.3cm −1 respectively. The beam combiner couples the two time-division scanned laser beams and divided them into three beams. One beam passed a reference cell filled with standard gases, and the other two beams transmitted to the open optical system consisting of the telescope and retro-reflector. The two optical systems used to measure respectively the gases absorption spectrum of background path and downwind path for quantitatively inverting the concentration. Temperatur e controller Current supply Signal processing module Detector1 Detector3 NH3 DFB laser Beam splitter Collimator Measurement open path Reference path Data acquisition processor DAC