img

官方微信

  • CN 62-1070/P
  • ISSN 1000-694X
  • 双月刊 创刊于1981年
高级检索
生物与土壤

黄土高原草地和农田生态系统碳滞留时间及固碳潜力

  • 郭丁 ,
  • 李旭东 ,
  • 王静 ,
  • 傅华
展开
  • 兰州大学 草地农业生态系统国家重点实验室/农业部草牧业创新重点实验室/草地农业科技学院, 甘肃 兰州 730020
郭丁(1986-),男,江苏宿迁人,讲师,主要从事草地生态学方面的研究。E-mail:dingg09@163.com

收稿日期: 2017-11-11

  修回日期: 2017-11-21

  网络出版日期: 2018-03-20

基金资助

国家重点研发计划项目(2016YFC0500505);国家自然科学基金项目(31502010,41671106,31201838);新疆维吾尔自治区重大科技专项(2016A03006);草地农业生态系统国家重点实验室开放基金项目(SKLGAE201401);中央高校基本科研业务费项目(lzujbky-2016-bt10,lzujbky-2017-kb11);"111"引智基地项目(B12002)

Estimation of Carbon Residence Times and Sequestration Potential of Grassland and Cropland Ecosystem in the Loess Plateau

  • Guo Ding ,
  • Li Xudong ,
  • Wang Jing ,
  • Fu Hua
Expand
  • State Key Laboratory of Grassland Agro-ecosystems/Key Laboratory of Grassland Livestock Industry Innovation/College of Pastoral Agriculture Science and Technology, Lanzhou University, Lanzhou 730020, China

Received date: 2017-11-11

  Revised date: 2017-11-21

  Online published: 2018-03-20

摘要

采用概率反演分析法估算黄土高原草地和农田生态系统各碳库滞留时间及固碳潜力。结果表明:除农田植物地上部分外,植物地上部分、地下部分、代谢性凋落物及土壤活性有机碳库滞留时间最短,为25~203 d;惰性凋落物碳库滞留时间为2.4~3 a;慢性有机碳库和惰性有机碳库滞留时间最长,分别为57.4~79.6 a和593~598 a。多年生草地的根系滞留时间显著高于农田;而农田代谢性凋落物碳库和慢性有机碳库的滞留时间显著高于草地。根据反演所得参数模拟,在当前气候和土壤条件下,农田和草地系统土壤有机碳在250 a左右时达稳定状态,农田系统固碳潜力约为2 680 g C·m-2,草地约为3 130 g C·m-2。农田有机肥的输入能使土壤有机碳多固定4 000 g C·m-2。有机肥的输入及土壤有机碳周转缓慢使耕作农田比草地更有利于土壤有机碳积累。

本文引用格式

郭丁 , 李旭东 , 王静 , 傅华 . 黄土高原草地和农田生态系统碳滞留时间及固碳潜力[J]. 中国沙漠, 2018 , 38(2) : 363 -371 . DOI: 10.7522/j.issn.1000-694X.2017.00111

Abstract

A Bayesian probability inversion was applied to estimate the Carbon residence times and sequestration potential of grassland and cropland ecosystems in the Loess Plateau. The result shows that the shortest Carbon residence times ranged from 25 to 203 days were in the aboveground and belowground biomass pools, the metabolic litter pools and the active soil organic matter (SOC) pools, excluding the aboveground biomass pool in cropland. The structure litter pools had Carbon residence times between 2.4 and 3 years. The longest Carbon residence times were 57.4-79.6 years and 593-598 years in the slow and passive SOC pools, respectively. Carbon residences times for the belowground biomass pools were longer in grassland than those in cropland, whereas Carbon residences times in the metabolic litter and slow SOC pools in grassland were shorter than those in cropland. According to the parameters derived from the inversion model, the SOC pools in grassland and cropland would reach a stable state in 250 years. The Carbon sequestration potential would be 3 130 and 2 680 g C·m-2, respectively, in grassland and cropland ecosystems. The application of manure could result in higher (4 000 g C·m-2) Carbon sequestration. Compared to that in grassland, the application of manure and the longer Carbon residence times of soil pools could lead to higher SOC sequestration in cropland ecosystem.

参考文献

[1] Luo Y Q,White L W,Canadell J G,et al.Sustainability of terrestrial carbon sequestration:a case study in Duke Forest with inversion approach[J].Global Biogeochemical Cycles,2003,17(1):1021-1034.
[2] Zhang L,Luo Y Q,Yu G R,et al.Estimated carbon residence times in three forest ecosystems of eastern China:applications of probabilistic inversion[J].Journal of Geophysical Research-Biogeosciences,2010,115:137-147.
[3] Farquhar G,von Caemmerer S v,Berry J.A biochemical model of photosynthetic CO2 assimilation in leaves of C3 species[J].Planta,1980,149(1):78-90.
[4] 马良,朱再春,曾辉.NPP评估过程模型应用研究进展[J].中国沙漠,2017,37(6):1250-1260.
[5] 张福平,冯起,李旭谱,等.黑河流域NPP遥感估算及其时空变化特征[J].中国沙漠,2014,34(6):1657-1664.
[6] 张涛,曹广超,曹生奎,等.2000-2012年青海湖流域NPP时空分布特征[J].中国沙漠,2015,35(4):1072-1080.
[7] Vogt K A,Vogt D J,Palmiotto P A,et al.Review of root dynamics in forest ecosystems grouped by climate,climatic forest type and species[J].Plant and soil,1996,187(2):159-219.
[8] 周涛,史培军,贾根锁,等.中国森林生态系统碳周转时间的空间格局[J].中国科学:地球科学,2010,40(5):632-644.
[9] Zhou T,Luo Y Q.Spatial patterns of ecosystem carbon residence time and NPP-driven carbon uptake in the conterminous United States[J].Global Biogeochemical Cycles,2008,22(3):1-15.
[10] 檀文炳,周力平,刘克新.基于土壤团聚体组分的14C分析及其在不同林龄土壤有机碳周转研究中的应用[J].科学通报,2013,58(14):1354-1366.
[11] Trumbore S.Age of soil organic matter and soil respiration:radiocarbon constraints on belowground C dynamics[J].Ecological Applications,2000,10(2):399-411.
[12] 于贵瑞,王秋凤,朱先进.区域尺度陆地生态系统碳收支评估方法及其不确定性[J].地理科学进展,2011,30(1):103-113.
[13] Xu T,White L,Hui D F,et al.Probabilistic inversion of a terrestrial ecosystem model:analysis of uncertainty in parameter estimation and model prediction[J].Global Biogeochemical Cycles,2006,20(2):1-15.
[14] 孙文娟,黄耀,张稳,等.农田土壤固碳潜力研究的关键科学问题[J].地球科学进展,2008,23(9):996-1004.
[15] 张黎,于贵瑞,Luo Y,等.基于模型数据融合的长白山阔叶红松林碳循环模拟[J].植物生态学报,2009,33(6):1044-1055.
[16] 李旭东,黄土高原草地与农田系统土壤呼吸及碳平衡[D].兰州:兰州大学,2011.
[17] Guo D,Li X,Li X,et al.Conventional tillage increases soil microbial biomass and activity in the Loess Plateau,China[J].Acta Agriculturae Scandinavica Section B-Soil and Plant Science,2013,63(6):489-496.
[18] Weng E S,Luo Y Q.Soil hydrological properties regulate grassland ecosystem responses to multifactor global change:a modeling analysis[J].Journal of Geophysical Research-Biogeosciences,2008,113:G03003.
[19] Parton W J,Schimel D S,Cole C,et al.Analysis of factors controlling soil organic matter levels in Great Plains grasslands[J].Soil Science Society of America Journal,1987,51(5):1173-1179.
[20] Zhou X H,Luo Y Q,Gao C,et al.Concurrent and lagged impacts of an anomalously warm year on autotrophic and heterotrophic components of soil respiration:a deconvolution analysis[J].New Phytologist,2010,187(1):184-198.
[21] Hastings W K.Monte Carlo sampling methods using Markov chains and their applications[J].Biometrika,1970,57(1):97-109.
[22] Metropolis N,Rosenbluth A W,Rosenbluth M N,et al.Equation of state calculations by fast computing machines[J].The journal of chemical physics,1953,21:1087-1092.
[23] Gelman A,Rubin D B.Inference from iterative simulation using multiple sequences[J].Statistical science,1992,7(4):457-472.
[24] Weng E S,Luo Y Q,Gao C,et al.Uncertainty analysis of forest carbon sink forecast with varying measurement errors:a data assimilation approach[J].Journal of Plant Ecology-Uk,2011,4(3):178-191.
[25] Matamala R,Gonz lez-Meler M a,Jastrow J D,et al.Impacts of fine root turnover on forest NPP and soil C sequestration potential[J].Science,2003,302(5649):1385-1387.
[26] Guo D,Wang J,Fu H,et al.Cropland has higher soil carbon residence time than grassland in the subsurface layer on the Loess Plateau,China[J].Soil & Tillage Research,2017,174:130-138.
[27] Sayer E J,Heard M S,Grant H K,et al.Soil carbon release enhanced by increased tropical forest litterfall[J].Nature Climate Change,2011,1(6):304-307.
[28] Dijkstra F A,Cheng W.Interactions between soil and tree roots accelerate long-term soil carbon decomposition[J].Ecology Letters,2007,10(11):1046-1053.
[29] Mann L.Changes in soil carbon storage after cultivation[J].Soil Science,1986,142(5):279-288.
[30] Davidson E A,Ackerman I L.Changes in soil carbon inventories following cultivation of previously untilled soils[J].Biogeochemistry,1993,20(3):161-193.
[31] Smith P.Land use change and soil organic carbon dynamics[J].Nutrient Cycling in Agroecosystems,2008,81(2):169-178.
[32] Guo L B,Gifford R M.Soil carbon stocks and land use change:a meta analysis[J].Global Change Biology,2002,8(4):345-360.
[33] Lal R.Soil carbon sequestration impacts on global climate change and food security[J].Science,2004,304(5677):1623-1627.
[34] 林飞燕,吴宜进,王绍强,等.秸秆还田对江西农田土壤固碳影响的模拟分析[J].自然资源学报,2013,28(6):981-993.
[35] Xu S,Shi X,Zhao Y,et al.Carbon sequestration potential of recommended management practices for paddy soils of China,1980-2050[J].Geoderma,2011,166(1):206-213.
[36] 覃章才,黄耀.基于模型的农田土壤固碳潜力估算[J].中国科学:生命科学,2010,40(7):658-676.
[37] Zhou X,Zhou T,Luo Y.Uncertainties in carbon residence time and NPP-driven carbon uptake in terrestrial ecosystems of the conterminous USA:a Bayesian approach[J].Tellus B,2012,64(5):577-583.
文章导航

/