Zones of influence for soil organic matter dynamics: A conceptual framework for data and models

被引:19
作者
Cagnarini, Claudia [1 ]
Blyth, Eleanor [2 ]
Emmett, Bridget A. [1 ]
Evans, Chris D. [1 ]
Griffiths, Robert, I [1 ]
Keith, Aidan [3 ]
Jones, Laurence [1 ]
Lebron, Inma [1 ]
McNamara, Niall P. [3 ]
Puissant, Jeremy [2 ]
Reinsch, Sabine [1 ]
Robinson, David A. [1 ]
Rowe, Edwin C. [1 ]
Thomas, Amy R. C. [1 ]
Smart, Simon M. [3 ]
Whitaker, Jeanette [3 ]
Cosby, Bernard J. [1 ]
机构
[1] Environm Ctr Wales, Ctr Ecol & Hydrol, Deiniol Rd, Bangor LL57 2UW, Gwynedd, Wales
[2] Ctr Ecol & Hydrol, Wallingford, Oxon, England
[3] Lancaster Environm Ctr, Ctr Ecol & Hydrol, Lancaster, England
基金
英国自然环境研究理事会;
关键词
conceptual framework; connectivity; soil depth; SOM model; SOM persistence; sustainable land management; UNSDG-15; zones of influence; CARBON-USE EFFICIENCY; MICROBIAL BIOMASS; STABILIZATION MECHANISMS; CLIMATE; SUBSOIL; NITROGEN; STOCKS; DECOMPOSITION; CONSTRAINTS; DEPOSITION;
D O I
10.1111/gcb.14787
中图分类号
X176 [生物多样性保护];
学科分类号
090705 ;
摘要
Soil organic matter (SOM) is an indicator of sustainable land management as stated in the global indicator framework of the United Nations Sustainable Development Goals (SDG Indicator 15.3.1). Improved forecasting of future changes in SOM is needed to support the development of more sustainable land management under a changing climate. Current models fail to reproduce historical trends in SOM both within and during transition between ecosystems. More realistic spatio-temporal SOM dynamics require inclusion of the recent paradigm shift from SOM recalcitrance as an 'intrinsic property' to SOM persistence as an 'ecosystem interaction'. We present a soil profile, or pedon-explicit, ecosystem-scale framework for data and models of SOM distribution and dynamics which can better represent land use transitions. Ecosystem-scale drivers are integrated with pedon-scale processes in two zones of influence. In the upper vegetation zone, SOM is affected primarily by plant inputs (above- and belowground), climate, microbial activity and physical aggregation and is prone to destabilization. In the lower mineral matrix zone, SOM inputs from the vegetation zone are controlled primarily by mineral phase and chemical interactions, resulting in more favourable conditions for SOM persistence. Vegetation zone boundary conditions vary spatially at landscape scales (vegetation cover) and temporally at decadal scales (climate). Mineral matrix zone boundary conditions vary spatially at landscape scales (geology, topography) but change only slowly. The thicknesses of the two zones and their transport connectivity are dynamic and affected by plant cover, land use practices, climate and feedbacks from current SOM stock in each layer. Using this framework, we identify several areas where greater knowledge is needed to advance the emerging paradigm of SOM dynamics-improved representation of plant-derived carbon inputs, contributions of soil biota to SOM storage and effect of dynamic soil structure on SOM storage-and how this can be combined with robust and efficient soil monitoring.
引用
收藏
页码:3996 / 4007
页数:12
相关论文
共 114 条
[1]   Contribution of sorption, DOC transport and microbial interactions to the 14C age of a soil organic carbon profile: Insights from a calibrated process model [J].
Ahrens, Bernhard ;
Braakhekke, Maarten C. ;
Guggenberger, Georg ;
Schrumpf, Marion ;
Reichstein, Markus .
SOIL BIOLOGY & BIOCHEMISTRY, 2015, 88 :390-402
[2]   Cheaters, diffusion and nutrients constrain decomposition by microbial enzymes in spatially structured environments [J].
Allison, SD .
ECOLOGY LETTERS, 2005, 8 (06) :626-635
[3]   Soil organic carbon stocks in topsoil and subsoil controlled by parent material, carbon input in the rhizosphere, and microbial-derived compounds [J].
Angst, Gerrit ;
Messinger, Johanna ;
Greiner, Maria ;
Haeusler, Werner ;
Hertel, Dietrich ;
Kirfel, Kristina ;
Koegel-Knabner, Ingrid ;
Leuschner, Christoph ;
Rethemeyer, Janet ;
Mueller, Carsten W. .
SOIL BIOLOGY & BIOCHEMISTRY, 2018, 122 :19-30
[4]  
[Anonymous], 2006, WORLD SOIL RES REP
[5]   Dilution limits dissolved organic carbon utilization in the deep ocean [J].
Arrieta, Jesus M. ;
Mayol, Eva ;
Hansman, Roberta L. ;
Herndl, Gerhard J. ;
Dittmar, Thorsten ;
Duarte, Carlos M. .
SCIENCE, 2015, 348 (6232) :331-333
[6]   Six months of L-terrestris L. activity in root-formed biopores increases nutrient availability, microbial biomass and enzyme activity [J].
Athmann, Miriam ;
Kautz, Timo ;
Banfield, Callum ;
Bauke, Sara ;
Hoang, Duyen T. T. ;
Luesebrink, Marcel ;
Pausch, Johanna ;
Amelung, Wulf ;
Kuzyakov, Yakov ;
Koepke, Ulrich .
APPLIED SOIL ECOLOGY, 2017, 120 :135-142
[7]  
Batjes NH, 2014, EUR J SOIL SCI, V65, P10, DOI [10.1111/j.1365-2389.1996.tb01386.x, 10.1111/ejss.12114_2]
[8]   An invasive wetland grass primes deep soil carbon pools [J].
Bernal, Blanca ;
Megonigal, J. Patrick ;
Mozdzer, Thomas J. .
GLOBAL CHANGE BIOLOGY, 2017, 23 (05) :2104-2116
[9]   Surface and subsurface microbial biomass, community structure and metabolic activity as a function of soil depth and season [J].
Blume, E ;
Bischoff, M ;
Reichert, JM ;
Moorman, T ;
Konopka, A ;
Turco, RF .
APPLIED SOIL ECOLOGY, 2002, 20 (03) :171-181
[10]   Lateral carbon transfer from erosion in noncroplands matters [J].
Borrelli, Pasquale ;
Panagos, Panos ;
Lugato, Emanuele ;
Alewell, Christine ;
Ballabio, Cristiano ;
Montanarella, Luca ;
Robinson, David A. .
GLOBAL CHANGE BIOLOGY, 2018, 24 (08) :3283-3284