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膜進(jìn)樣質(zhì)譜儀

膜進(jìn)樣質(zhì)譜儀
詳細(xì)信息

美國自然基金委推薦測量濕地脫氮速率專用儀器

反硝化速率和脫氮速率科研的強(qiáng)大工具

高精度溶解氣體測量儀器


前言:

氮?dú)猓∟2)、氧氣(O2)、二氧化碳(CO2)是濕地、河流、湖泊、海洋等水體中的重要溶解氣體,是生態(tài)環(huán)境變化過程中的重要參數(shù)指標(biāo)。例如,溶解氧是衡量海氣擴(kuò)散過程、水團(tuán)混合、大洋環(huán)流以及海水中生物化學(xué)過程的重要指標(biāo);水體中CO2對于研究全球碳循環(huán)和全球氣候變化具有重要作用;而水體中溶解N2則對于研究水體反硝化速率、農(nóng)業(yè)氮肥利用率、水體富營養(yǎng)化等相關(guān)問題具有至關(guān)重要的作用。目前,測量水體海洋中溶解氣體的傳統(tǒng)方法是先采集水樣,然后在實(shí)驗(yàn)室內(nèi)或者船上進(jìn)行檢測,但由于很多參數(shù)會隨時(shí)空的變化而發(fā)生改變,從而得不到實(shí)時(shí)原位的準(zhǔn)確數(shù)據(jù)。水體及沉積物反硝化速率的測定方法主要有乙炔抑制法、N2通量法、質(zhì)量平衡法、化學(xué)計(jì)量法和同位素法,但這些方法大多存在人為擾動大、操作繁瑣、誤差大的不足,因而無法精確測定淹水環(huán)境下的反硝化速率。膜進(jìn)樣質(zhì)譜儀(MIMS)則能夠?qū)崟r(shí)、原位、連續(xù)監(jiān)測水體中的溶解氣體(N2、O2、CO2),并且能夠精確測定淹水環(huán)境下水體、沉積物的反硝化速率,已被國內(nèi)外眾多研究機(jī)構(gòu)廣泛應(yīng)用,并被美國自然科學(xué)基金委推薦用來測定濕地脫氮速率。同時(shí),膜進(jìn)樣質(zhì)譜儀還能夠應(yīng)用于穩(wěn)定同位素(15N 、18O、13C)的檢測、光合呼吸、生物反應(yīng)器等方面的研究。


主要特點(diǎn):

  • 可實(shí)時(shí)、原位檢測
  • 測量精度高、重復(fù)性好
  • 所需樣品量少,僅5ml
  • 操作簡便,樣品分析快,僅90s
  • 不需要頂空平衡,可實(shí)現(xiàn)水氣分離
  • 可將空氣中高濃度背景氣體分離開,避免了樣品的污染
  • 專用軟件(QuickData)高效評估收集的信號和數(shù)據(jù)


圖1 QuickData軟件


主要應(yīng)用:

  • 環(huán)境(水體、沉積物)反硝化速率的研究
  • 原位測量水體(海洋\湖泊\河流\地表水\地下水)中O2、CH4、DMS、CO2和Ar濃度
  • 海洋總初級生產(chǎn)力的測定
  • 貧瘠水域的呼吸作用研究
  • 穩(wěn)定同位素的測定(15N 、18O、13C)


圖2   MIMS在反硝化中的應(yīng)用,將原狀沉積物和上覆水取回在室內(nèi)進(jìn)行培養(yǎng),研究反硝化過程中N2的排放速率

圖3   利用已知CH4濃度和測量出來的信號值進(jìn)行擬合曲線,進(jìn)而測量未知水體中CH4濃度


圖4   MIMS可用于水生生態(tài)系統(tǒng)代謝和氧氣動力學(xué)研究


圖5   MIMS可與液相氧電極或葉綠素?zé)晒鈨x聯(lián)用測量光合和呼吸作用



MIMS典型應(yīng)用:


表1   標(biāo)樣連續(xù)測定10h后信號偏移情況(李曉波等,2013)


表2   MIMS與IRMS在測量海洋總初級生產(chǎn)力時(shí)的數(shù)據(jù)比較


圖7   利用MIMS測量出11種中國典型稻田土壤下的反硝化、厭氧氨氧化、DNRA的貢獻(xiàn)率(Shan J et. al, 2016)


參考文獻(xiàn):


1.李曉波, 夏永秋, 郎漫, 等. N2:Ar法直接測定淹水環(huán)境反硝化產(chǎn)物N2的產(chǎn)生速率. 農(nóng)業(yè)環(huán)境科學(xué)學(xué)報(bào), 2013, 32(6): 1284-1288

2.趙永強(qiáng), 夏永秋, 李博倫, 等. 利用膜進(jìn)樣質(zhì)譜同時(shí)測定河流沉積物反硝化和厭氧氨氧化. 農(nóng)業(yè)環(huán)境科學(xué)學(xué)報(bào), 2014, 33(4): 794-802

3.Alexandra M F R, Matthew A C. Benthic nitrogen fixation in an eutrophic estuary affected by groundwater discharge. Journal of Coastal Research, 2012, 28(2): 477-485

4. Alexander J R, Jennifer L T, Timothy J H, et al. Sediment, water column, and open-channel denitrification in rivers measured using membrane-inlet mass spectrometry. Journal of Geophysical Research: Biogeosciences, 2015, 121: 1258 -1274

5.Fred J G, Dragoslav T M, John C L. Estimating rates of denitrification enzyme activity in wetland soils with direct simultaneous quantification of nitrogen and nitrous oxide by membrane inlet mass spectrometry. Microbial & Biochemical Technology, 2013, 5(4): 095-101

6. Gueguen C, Tortell P D. High-resolution measurement of Southern Ocean CO2 and O2/Ar by membrane inlet mass spectrometry[J]. Marine Chemistry, 2008, 108(3/4): 184-194

7. Jeffrey C C, Michael K, Todd M K. Denitrification in coastal ecosystems: methods, environmental controls, and ecosystem level controls, a review. Aquatic Ecology, 1999, 33: 41-54

8. Jun S, Xu Z, Rong S, et al. Dissimilatory nitrate reduction processes in typical Chinese paddy soils: rates, relative contributions, and influencing factors. Environmental Science & Technology, 2016, 50: 9972-9980

9. Kaiser J, Reuer M K, Barnett B, et al. Marine productivity estimates from continuous O2/Ar ratio measurements bymembrane inlet mass spectromtry[J]. Geophysical Reasearch Letters, 2005, 32(19), doi: 10. 1029/2005GL023459

10. Ketil K J, Anne E G. New approach for measuring denitrification in the rhizosphere of vegetated marsh sediments. Limnology and Oceanography: Methods, 2009, 7: 626-637

11. Lesley K S, Mary A V, John K B, et al. Denitrification in nitrate-rich streams: application of N2:Ar and 15N-tracer methods in intact cores. Eeological Applications, 2006, 16(6):  2191-2207

12. Mohammad L K, Karl G R. Denitrification enzyme activity and potential of subsoils under grazed grasslands assayed by membrane inlet mass spectrometer. Soils Biology & Biochemistry, 2011, (43):1787-1797

13. Peter M G, Mark A A, Bohlke J K, et al. Methods for measuring denitrification: diverse approaches to A difficult problem. Ecological Applications, 2006, 16(6): 2091-2122

14. Reisinger A J, Tank J L, Hoellein T J, et al. Sediment, water column, and open‐channel denitrification in rivers measured using membrane‐inlet mass spectrometry[J]. Journal of Geophysical Research: Biogeosciences, 2016, 121(5): 1258-1274

15. Sara F, Daniela A V, Karin M B, et al. Application of membrane inlet mass spectrometry to measure aquatic gross primary production by the 18O in vitro method. Limnology and Oceanography: Methods, 2016, 14: 610-622

16. Shan J, Zhao X, Sheng R, et al. Dissimilatory nitrate reduction processes in typical Chinese paddy soils: rates, relative contributions, and influencing factors. Environmental Sciences & Technology, 2016, 50: 9972-9980

17. Sooomo A, Wayne S G, Todd M K. Simultaneous measurement of denitrification and nitrogen fixation using isotope pairing with membrane inlet mass spectrometry analysis. Applied and Environmental Microbiology, Mar. 2001, p. 1171-1178

18. Todd M K, Christina D, Hunt D, et al. Membrane inlet mass spectrometer for rapid high-precision determination of N2, O2, and Ar in environmental water samples. Analytical Chemistry, 1994, 66(23): 4166-4170

19. Todd K M, Cornwell J C, Zhong L. Determination of denitrification in the Chesapeake Bay from measurements of N2 accumulation in bottom water[J]. Estuaries and Coasts, 2006, 29(2): 222-231.

20. Todd M K, Matthew B S, Jeffrey C C, et al. Denitrification in estuarine sediments determined by membrane inlet mass spectrometry. Limnology and Oceanography, 1998, 43(2): 334-339

21. Tortell P D. Dissolved gas measurements in oceanic waters made by membrane inlet mass spectrometry[J]. Limnology and Oceanography: Methods, 2005, 3(1): 24-37

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