采集闽江河口淡水芦苇(Phragmites australis)沼泽湿地土壤,添加人造海水稳定3个月后“构造”盐度分别为0‰、2.5‰、11‰和22‰的湿地土壤,以上盐度值分别位于河口区淡水、寡咸水、中咸水和多咸水沼泽湿地的盐度分区范围.室内运用微宇宙(microcosm)厌氧培养实验,并分别添加铵态氮和硝酸盐氮,以期揭示盐度在不同形态氮输入对河口感潮沼泽湿地土壤CH4和CO2产生速率的影响的角色.盐度、施氮形态对河口沼泽湿地土壤BG、CBH、NAG、PHO、PEO和mcrA的活性具有显著的影响,添加铵态氮和硝酸盐氮显著增加沼泽湿地不同盐度土壤的CBH、NAG和mcrA的活性.与对照组相比,添加铵态氮显著增加淡水、寡咸水和中咸水沼泽湿地土壤CH4产生速率,分别增加21.9%、23.6% 和40.4%,但对多咸水土壤无显著影响;添加硝酸盐氮后淡水、寡咸水、中咸水土壤CH4产生速率分别降低16.56%、15.56% 和19.28%,添加硝酸盐氮显著降低多咸水湿地CH4产生速率19.7%.铵态氮和硝酸盐氮输入显著增加寡咸水和中咸水土壤CO2产生速率,而对淡水和多咸水土壤CO2产生速率无影响. 施氮情景下,沼泽土壤CH4和CO2产生速率与pH值、土壤胞外酶活性和mcrA丰度呈显著正相关,与盐度、SOC、Cl−和SO42−呈显著负相关.随机森林模型结果显示,施氮情景下,盐度、NAG、SO42−和pH值对CH4和CO2产生速率贡献率最大.研究结果说明:氮负荷增加对于河口区不同盐度沼泽湿地土壤CH4和CO2产生速率的影响不同,今后在制定减缓河口区富营养化对河口沼泽湿地温室气体排放影响的对策和措施时,应考虑到盐度梯度的影响.
Abstract
In this study, we collected soil samples from the freshwater Phragmites australis marsh at the Minjiang River estuary and constructed wetland soils with different salinities of 0‰, 2.5‰, 11‰, and 22‰ by adding artificial seawater and stabilizing for three months. These salinity values correspond to the ranges of fresh, oligohaline, mesohaline, and polyhaline water zones in estuarine tidal wetlands, respectively. We conducted indoor microcosm anaerobic incubation experiments and meanwhile added ammonium and nitrate to determine role of salinity in the impact of nitrogen additions on CH4 and CO2 production in estuarine tidal marsh soils. The results showed that the salinity and nitrogen form had significant effects on the activities of BG, CBH, NAG, PHO, PEO, and mcrA, the addition of ammonium and nitrate significantly increased activities of CBH, NAG, and mcrA in the soils with different salinities. Ammonium addition significantly increased CH4 production rates in the fresh, oligohaline, and mesohaline water marsh soils by 21.9%, 23.6%, and 40.4%, respectively, but had no significant effect on polyhaline soil. Nitrate addition decreased CH4production rates in the fresh, oligohaline, and mesohaline soils by 16.56%、15.56% and 19.28%, respectively, although the drop were not significant (P>0.05), nitrate addition significantly reduced CH4production rates in polyhaline soil by 19.7%. Both ammonium and nitrate addition significantly increased CO2 production rates in oligohaline and mesohaline soil, while did not significantly change the CO2 production rates in the fresh and polyhaline soil. Under the nitrogen addition, the production rates of CH4 and CO2 were significantly positively correlated with soil pH, extracellular enzyme activities, and mcrA abundance, and significantly negatively correlated with salinity, SOC, Cl−, and SO42−. The results of random forest model prediction showed that under nitrogen addition scenarios, salinity, NAG, SO42−, and pH had the greatest contribution rates to the production rates of CH4and CO2.Our results indicate that the impact of nitrogen input on CH4 and CO2 production rates of estuarine marsh soils varies with salinity. In future, we should consider the influence of salinity gradients when making the strategies and measures to mitigate impact of eutrophication on greenhouse gas emission.
关键词
CH4产生速率 /
CO2产生速率 /
氮输入 /
盐度 /
沼泽湿地 /
河口
Key words
CH4 production rates /
CO2 production rates /
nitrogen addition /
salinity /
marsh /
estuary
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参考文献
[1] IIPCC, 2022. Climate change 2022: Mitigation of climate change [R]. Cambridge University Press, Cambridge, UK and New York, NY, USA.
[2] Segarra K E A, Comerford C, Slaughter J, et al. Impact of electron acceptor availability on the anaerobic oxidation of methane in coastal freshwater and brackish wetland sediments [J]. Geochimica et Cosmochimica Acta, 2013,115:15-30.
[3] 肖 颖,杨继松.辽河口滨海湿地土壤有机碳矿化及其与盐分的关系 [J]. 生态学杂志, 2015,34(10):2792-2798. Xiao Y, Yang J S. Soil organic carbon mineralization and its relation with salinity in coastal wetland of Liaohe estuary [J]. Chinese Journal of Ecology, 2013,115:15-30.
[4] Bouillon S, Borges A V, Casta eda-moyae, et al. Mangrove production and carbon sinks: A revision of global budget estimates [J]. Global Biogeochemical Cycles, 2008,22:1-12.
[5] Huang Y, Ciais P, Luo Y, et al. Trade off of CO2 and CH4 emissions from global peatlands under water-table drawdown [J]. Nature Climate Change, 2021,11(7):618-622.
[6] Vivanco L A, Irvine I C, Martiny J B. Nonlinear responses in salt marsh functioning to increased nitrogen addition [J]. Ecology, 2015,96(4):936-947.
[7] Hu Y, Zheng Q, Noll L, et al. Direct measurement of the in situ decomposition of microbial-derived soil organic matter [J]. Soil Biology and Biochemistry, 2020,141:107660.
[8] Zhou M, Butterbach-Bahl K, Vereecken H, et al. A meta-analysis of soil salinization effects on nitrogen pools, cycles and fluxes in coastal ecosystems [J]. Global change biology, 2017,23(3):1338-1352.
[9] Wen X, Chen X, Jing X, et al. A meta-analysis of soil extracellular enzyme activities in response to global change [J]. Soil Biology and Biochemistry, 2018,123:21-32.
[10] Yin Z, Yu X, Zou Y, et al. Nitrogen addition effects on wetland soils depend on environmental factors and nitrogen addition methods: A meta-analysis [J]. Water, 2022,14(11):1748.
[11] Hu M J, Wilson B J, Sun Z G, et al.Effects of the addition of nitrogen and sulfate on CH4 and CO2 emissions, soil, and pore water chemistry in a high marsh of the Min River Estuary in southeastern China [J]. Science of the Total Environment, 2017,579:292-304.
[12] Kim J, Chaudhary D R, Kang H. Nitrogen addition differently alters GHGs production and soil microbial community of tidal salt marsh soil depending on the types of halophyte [J]. Applied Soil Ecology, 2020,150:103440.
[13] Larmola T, Leppänen S M, Tuittila E S, et al. Methanotrophy induces nitrogen fixation during peatland development [J]. Proceedings of the National Academy of Sciences of the United States of America, 2014,111(2):734-739.
[14] Lucía V, Irvine Irina C, Martiny Jennifer B H.Nonlinear responses in salt marsh functioning to increased nitrogen addition [J]. Ecology, 2015,96(4):936-947.
[15] Bodelier P L E, Laanbroek H J. Nitrogen as a regulatory factor of methane oxidation in soils and sediments [J]. FEMS Microbiology Ecology, 2004,47(3):265-277.
[16] Liu L L, Greaver T L. A review of nitrogen enrichment effects on three biogenic GHGs: the CO2 sink may be largely offset by stimulated N2O and CH4 emission [J]. Ecology Letters, 2009,12(10):1103-1117.
[17] Deng L, Huang C, Kim D G, et al. Soil GHG fluxes are altered by N deposition: New data indicate lower N stimulation of the N2O flux and greater stimulation of the calculated C pools [J]. Global Change Biology, 2020,26(4):2613-2629.
[18] Wu J, Cheng X, Xing W, et al. Soil-atmosphere exchange of CH4 in response to nitrogen addition in diverse upland and wetland ecosystems: A meta-analysis [J]. Soil Biology and Biochemistry, 2022, 164:108467.
[19] Dong H, Yao Z, Zheng X, et al. Effect of ammonium-based, non- sulfate fertilizers on CH4 emissions from a paddy field with a typical Chinese water management regime [J]. Atmospheric Environment, 2011,45(5):1095-1101.
[20] Yao Z, Zheng X, Dong H, et al. A 3-year record of N2O and CH4 emissions from a sandy loam paddy during rice seasons as affected by different nitrogen application rates [J]. Agriculture, ecosystems & environment, 2012,152:1-9.
[21] Morris J, Ye R Z, Silva L C R, et al. Nitrogen fertilization had no effect on CH4 and N2O emissions in rice planted in rewetted peatlands [J]. Soil Science Society of America Journal, 2017,81:224-232.
[22] 仝 川,罗 敏,谭 季.湿地甲烷代谢对氮输入响应的复杂性及其机制分析 [J]. 生态学报, 2024,44(4):1324-1335. Tong C, Luo M, Tan J. Complexity of effects of nitrogen input on methane metabolism in wetlands and mechanism analysis [J]. Acta Ecologica Sinica, 2024,44(4):1324-1335.
[23] 曾志华,杨民和,佘晨兴,等.闽江河口区淡水和中盐水潮汐沼泽湿地土壤产甲烷菌多样性 [J]. 生态学报, 2014,34(10):2674-2681. Zeng Z H, Yang M H, Yu X C, et al. Diversity of methanogen communities in tidal freshwater and brackish marsh soil in the Min River estuary [J]. Acta Ecologica Sinica, 2014,34(10):2674-2681.
[24] 王 纯,刘兴土,仝 川,等.水盐梯度对闽江河口湿地土壤有机碳组分的影响 [J]. 中国环境科学, 2017,37(10):3919-3928. Wang C, Liu X S, Tong C, et al. Effects of hydrologic and salinity gradients on soil organic carbon composition in Min River Estuarine wetland [J]. China Environmental Science, 2017,37(10):3919-3928.
[25] Chambers L G, Osborne T Z, Reddy K R. Effect of salinity-altering pulsing events on soil organic carbon loss along an intertidal wetland gradient: a laboratory experiment [J]. Biogeochemistry, 2013,115:363- 383.
[26] Dang C, Morrissey E M, Neubauer S C, et al. Novel microbial community composition and carbon biogeochemistry emerge over time following saltwater intrusion in wetlands [J]. Global change biology, 2019,25(2):549-561.
[27] Servais S, Kominoski J S, Charles S P, et al. Saltwater intrusion and soil carbon loss: Testing effects of salinity and phosphorus loading on microbial functions in experimental freshwater wetlands [J]. Geoderma, 2019,337:1291-1300.
[28] Neubauer S C, Franklin R B, Berrier D J. Saltwater intrusion into tidal freshwater marshes alters the biogeochemical processing of organic carbon [J]. Biogeosciences, 2013,10(12):8171-8183.
[29] Baldwin D S, Rees G N, Mitchell A M, et al. The short-term effects of salinization on anaerobic nutrient cycling and microbial community structure in sediment from a freshwater wetland [J]. Wetlands, 2006, 26:455–464.
[30] Vizza C, West W E, Jones S E, et al. Regulators of coastal wetland methane production and responses to simulated global change [J]. Biogeosciences, 2017,14(2):431-446.
[31] Minick K J, Mitra B, Noormets A, et al. Saltwater reduces potential CO2 and CH4 production in peat soils from a coastal freshwater forested wetland [J]. Biogeosciences, 2019,16(23):4671-4686.
[32] Marton J M, Herbert E R, Craft C B. Effects of salinity on denitrification and greenhouse gas production from laboratory- incubated tidal forest soils [J]. Wetlands, 2012,32:347-357.
[33] Odum W E. Comparative ecology of tidal freshwater and salt marshes [J]. Annual Review of Ecology and Systematics, 1988,19:147-176.
[34] Bergman I, Klarqvist M, Nilsson M. Seasonal variation in rates of methane production from peat of various botanical origins: Effects of temperature and substrate quality [J]. FEMS Microbiology Ecology, 2000,33(3):181-189.
[35] Mou X, Liu X, Sun Z, et al. Short-term effect of exogenous nitrogen on N2O fluxes from native and invaded tidal marshes in the Min River Estuary, China [J]. Wetlands, 2019,39:139-148.
[36] Kim J, Chaudhary D R, Kang H. Nitrogen addition differently alters GHGs production and soil microbial community of tidal salt marsh soil depending on the types of halophyte [J]. Applied Soil Ecology, 2020,150:103440.
[37] Wassmann R, Neue H U, Bueno C, et al. Methane production capacities of different rice soils derived from inherent and exogenous substrates [J].Plant and Soil, 1998,203(2):227-237.
[38] 鲁如坤.土壤农业化学分析方法 [M]. 北京:中国农业科技出版社, 2000:269-290. Lu R K.Methods of Soil and Agro-Chemical Analysis [M]. China Agricultural Science and Technology Press, 2000:269-290.
[39] Saiya-Cork K R, Sinsabaugh R L, Zak D R, et al. The effects of long-term nitrogen deposition on extracellular enzyme activity in an Acer saccharum forest soil [J]. Soil Biology and Biochemistry, 2002, 34(9):1309-1315.
[40] Steinberg L M, Regan J M. mcrA -targeted real-time quantitative PCR method to examine methanogen communities [J]. Applied and Environmental Microbiology, 2009,75(13):4435-4442.
[41] Wallenstein M D, Burns R G. Ecology of extracellular enzyme activities and organic matter degradation in soil: A complex community- driven process [J]. Methods of soil enzymology, 2011,9:35-55.
[42] Burns R G, DeForest J L, Marxsen J, et al. Soil enzymes in a changing environment: Current knowledge and future directions [J]. Soil Biology and Biochemistry, 2013,58:216-234.
[43] Vallcro M V G, Pol L W H, Lettinga G, et al. Effect of NaCl on thermophilic (55℃) methanol degradation in sulfate reducing granular sludge reactors [J]. Water Research, 2003,37(10):2269-2280.
[44] Soong J L, Marañon-Jimenez S, Cotrufo M F, et al. Soil microbial CNP and respiration responses to organic matter and nutrient additions: evidence from a tropical soil incubation [J]. Soil Biology and Biochemistry, 2018,122:141-149.
[45] Hobbie J E, Hobbie E A. Microbes in nature are limited by carbon and energy: the starving-survival lifestyle in soil and consequences for estimating microbial rates [J]. Front Microbiol, 2013,12(4):324.
[46] Jian S, Li J, Chen J I, et al. Soil extracellular enzyme activities [J]. soil carbon and nitrogen storage, 2016,101:32-43.
[47] Shackle V J, Freeman C, Reynolds B. Carbon supply and the regulation of enzyme activity in constructed wetlands [J]. Soil Biology and Biochemistry, 2000,32(13):1935-1940.
[48] Yang S, Xu Z, Wang R, et al. Variations in soil microbial community composition and enzymatic activities in response to increased N deposition and precipitation in Inner Mongolian grassland [J]. Applied Soil Ecology, 2017,119:275-285.
[49] Nan Q, Fang C, Cheng L, et al. Elevation of NO3−N from biochar amendment facilitates mitigating paddy CH4 emission stably over seven years [J]. Environmental Pollution, 2022,295:118707.
[50] Ni Y, Zheng Y, Hou L, et al. Microbial dynamics and activity of denitrifying anaerobic methane oxidizers in China's estuarine and coastal wetlands [J]. Science of The Total Environment, 2022,806:150425.
[51] 展鹏飞,黄佳芳,佘晨兴,等.脉冲式盐水及Fe(Ⅲ)施加对河口感潮淡水湿地土壤产甲烷菌和硫酸盐还原菌群落结构和数量的影响 [J]. 环境科学学报, 2020.40(7):2599-2610. Zhan P F, Huang J F, Yu C X, et al. Effects of saltwater and Fe(Ⅲ) pulses on community structure and abundance of methanogens and sulfate-reducing bacteria in tidal freshwater marsh of the Min River estuary [J]. Acta Scientiae Circumstantiae, 2020,40(7):2599-2610.
[52] Tao B, Song C, Guo Y.Short-term effects of nitrogen additions and increased temperature on wetland soil respiration, Sanjiang Plain, China [J]. Wetlands, 2013,33(4):727-736.
[53] 白军红,刘 玥,赵庆庆,等.水盐变化对滨海湿地土壤有机碳累积与碳排放的影响综述 [J]. 北京师范大学学报(自然科学版), 2022, 58(3):447-457. Bai J H, Liu Y, Zhao Q Q, et al. Soil organic carbon accumulation and decomposition in coastal wetlands in the changing water and salinity conditions: a review [J]. Beijing Normal University, 2022,58(3):447-457.
[54] Zhao Q, Bai J, Zhang G, et al. Effects of water and salinity regulation measures on soil carbon sequestration in coastal wetlands of the Yellow River Delta [J]. Geoderma, 2018,319:219-229.
[55] Tollefson J. Scientists raise alarm over'dangerously fast' growth in atmospH值eric methane [J]. Nature, 2022.
[56] Du Y, Guo P, Liu J, et al. Different types of nitrogen deposition show variable effects on the soil carbon cycle process of temperate forests [J]. Global change biology, 2014,20(10):3222-3228.
[57] Yuan J, Liu D, Ji Y, et al. Spartina alterniflora invasion drastically increases methane production potential by shifting methanogenesis from hydrogenotrophic to methylotrophic pathway in a coastal marsh [J]. Journal of Ecology, 2019,107(5):2436-2450.
[58] Ye R Z, Jin Q S, Bohannan B, et al. pH controls over anaerobic carbon mineralization, the efficiency of methane production, and methanogenic pathways in peatlands across an ombrotrophic- minerotrophic gradient [J]. Soil Biology and Biochemistry, 2012,54:36-47.
[59] Söderberg K H, Baath E. The influence of nitrogen fertilisation on bacterial activity in the rhizosphere of barley [J]. Soil Biology and Biochemistry, 2004,36(1):195-198.
[60] Kotsyurbenko O R, Friedrich M W, Simankova M V, et al.Shift from acetoclastic to H2-dependent methanogenesis in a West Siberian peat bog at low ph values and isolation of an acidophilic Methanobacterium strain [J]. Applied and Environmental Microbiology, 2007,73(7):2344-2348.
[61] Bernhard A E, Dwyer C, Idrizi A, et al. Long-term impacts of disturbance on nitrogen-cycling bacteria in a New England salt marsh [J]. Frontiers in Microbiology, 2015,6:46.
[62] Teixeira C, Magalhães C, Joye S B, et al. The role of salinity in shaping dissolved inorganic nitrogen and N2O dynamics in estuarine sediment–water interface [J]. Marine pollution bulletin, 2013,66(1/2): 225-229.
[63] Reay D S, Nedwell D B. Methane oxidation in temperate soils: effects of inorganic N [J]. Soil Biology and Biochemistry, 2004,36(12):2059- 2065.
[64] Paul L E, Bodelier, Hendrikus J, et al. Nitrogen as a regulatory factor of methane oxidation in soils and sediments [J]. FEMS Microbiology Ecology, 2004,47:265-277.
基金
国家自然科学基金资助项目(42177213);国家重点研发计划项目(2022YFC3105401);中央专项财政支持项目([350182]FJYHZB[GK]2024001)