Carbon Storage Along with Soil Profile: an Example of Soil Chronosequence from the Fluvial Terraces on the Pakua Tableland, Taiw
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Dynamics of Carbon 14 in Soils: a Review C
Radioprotection, Suppl. 1, vol. 40 (2005) S465-S470 © EDP Sciences, 2005 DOI: 10.1051/radiopro:2005s1-068 Dynamics of Carbon 14 in soils: A review C. Tamponnet Institute of Radioprotection and Nuclear Safety, DEI/SECRE, CADARACHE, BP. 1, 13108 Saint-Paul-lez-Durance Cedex, France, e-mail: [email protected] Abstract. In terrestrial ecosystems, soil is the main interface between atmosphere, hydrosphere, lithosphere and biosphere. Its interactions with carbon cycle are primordial. Information about carbon 14 dynamics in soils is quite dispersed and an up-to-date status is therefore presented in this paper. Carbon 14 dynamics in soils are governed by physical processes (soil structure, soil aggregation, soil erosion) chemical processes (sequestration by soil components either mineral or organic), and soil biological processes (soil microbes, soil fauna, soil biochemistry). The relative importance of such processes varied remarkably among the various biomes (tropical forest, temperate forest, boreal forest, tropical savannah, temperate pastures, deserts, tundra, marshlands, agro ecosystems) encountered in the terrestrial ecosphere. Moreover, application for a simplified modelling of carbon 14 dynamics in soils is proposed. 1. INTRODUCTION The importance of carbon 14 of anthropic origin in the environment has been quite early a matter of concern for the authorities [1]. When the behaviour of carbon 14 in the environment is to be modelled, it is an absolute necessity to understand the biogeochemical cycles of carbon. One can distinguish indeed, a global cycle of carbon from different local cycles. As far as the biosphere is concerned, pedosphere is considered as a primordial exchange zone. Pedosphere, which will be named from now on as soils, is mainly located at the interface between atmosphere and lithosphere. -
Soil Carbon Science for Policy and Practice Soil-Based Initiatives to Mitigate Climate Change and Restore Soil Fertility Both Rely on Rebuilding Soil Organic Carbon
comment Soil carbon science for policy and practice Soil-based initiatives to mitigate climate change and restore soil fertility both rely on rebuilding soil organic carbon. Controversy about the role soils might play in climate change mitigation is, consequently, undermining actions to restore soils for improved agricultural and environmental outcomes. Mark A. Bradford, Chelsea J. Carey, Lesley Atwood, Deborah Bossio, Eli P. Fenichel, Sasha Gennet, Joseph Fargione, Jonathan R. B. Fisher, Emma Fuller, Daniel A. Kane, Johannes Lehmann, Emily E. Oldfeld, Elsa M. Ordway, Joseph Rudek, Jonathan Sanderman and Stephen A. Wood e argue there is scientific forestry, soil carbon losses via erosion and carbon, vary markedly within a field. Even consensus on the need to decomposition have generally exceeded within seemingly homogenous fields, a Wrebuild soil organic carbon formation rates of soil carbon from plant high spatial density of soil observations is (hereafter, ‘soil carbon’) for sustainable land inputs. Losses associated with these land therefore required to detect the incremental stewardship. Soil carbon concentrations and uses are substantive globally, with a mean ‘signal’ of management effects on soil carbon stocks have been reduced in agricultural estimate to 2-m depth of 133 Pg carbon8, from the local ‘noise’11. Given the time soils following long-term use of practices equivalent to ~63 ppm atmospheric CO2. and expense of acquiring a high density of such as intensive tillage and overgrazing. Losses vary spatially by type and duration observations, most current soil sampling is Adoption of practices such as cover crops of land use, as well as biophysical conditions too limited to reliably quantify management and silvopasture can protect and rebuild such as soil texture, mineralogy, plant effects at field scales9,10. -
Agricultural Soil Carbon Credits: Making Sense of Protocols for Carbon Sequestration and Net Greenhouse Gas Removals
Agricultural Soil Carbon Credits: Making sense of protocols for carbon sequestration and net greenhouse gas removals NATURAL CLIMATE SOLUTIONS About this report This synthesis is for federal and state We contacted each carbon registry and policymakers looking to shape public marketplace to ensure that details investments in climate mitigation presented in this report and through agricultural soil carbon credits, accompanying appendix are accurate. protocol developers, project developers This report does not address carbon and aggregators, buyers of credits and accounting outside of published others interested in learning about the protocols meant to generate verified landscape of soil carbon and net carbon credits. greenhouse gas measurement, reporting While not a focus of the report, we and verification protocols. We use the remain concerned that any end-use of term MRV broadly to encompass the carbon credits as an offset, without range of quantification activities, robust local pollution regulations, will structural considerations and perpetuate the historic and ongoing requirements intended to ensure the negative impacts of carbon trading on integrity of quantified credits. disadvantaged communities and Black, This report is based on careful review Indigenous and other communities of and synthesis of publicly available soil color. Carbon markets have enormous organic carbon MRV protocols published potential to incentivize and reward by nonprofit carbon registries and by climate progress, but markets must be private carbon crediting marketplaces. paired with a strong regulatory backing. Acknowledgements This report was supported through a gift Conservation Cropping Protocol; Miguel to Environmental Defense Fund from the Taboada who provided feedback on the High Meadows Foundation for post- FAO GSOC protocol; Radhika Moolgavkar doctoral fellowships and through the at Nori; Robin Rather, Jim Blackburn, Bezos Earth Fund. -
Measuring Soil Carbon Change
Measuring soil carbon change Peter Donovan version: October 2013 This guide can be freely copied and adapted, with attribution, no commercial use, and derivative works similarly licensed. Contents What this guide is about, and how to use it iv 1 The work of the biosphere 1 1.1 Technology . 1 1.2 The carbon cycle . 2 1.3 Let, not make . 3 1.4 Monitoring: a strategic and creative choice . 4 2 Measuring soil carbon 7 2.1 Purpose, result, and uncertainty . 7 2.2 Change . 9 2.3 Organic and inorganic soil carbon . 11 2.4 Laboratory tests . 12 2.5 Getting started . 14 3 Site selection and sampling design 15 3.1 Mapping your site . 15 3.2 Stratification . 15 3.3 Locating plots . 17 3.4 Sampling tools . 17 3.5 Sampling intensity within the plot . 17 4 Sampling and field procedures 20 4.1 Lay out a transect and mark the plot center . 20 4.2 Soil surface observations . 23 4.3 Lay out the plot . 23 4.4 Use probe to take samples . 24 4.5 Soils with abundant rocks, gravel, or coarse fragments . 24 4.6 Characterize the soil . 25 4.7 Bag the sample . 26 4.8 Going deeper . 26 4.9 Sampling for bulk density . 27 4.10 Resampling . 29 4.11 Correcting for changes in bulk density . 29 ii 5 Getting your samples analyzed 31 5.1 Sample preparation . 31 5.2 Storing samples . 32 5.3 Split sampling to test your lab . 32 5.4 U.S. labs that do elemental analysis or dry combustion test . -
Progressive and Regressive Soil Evolution Phases in the Anthropocene
Progressive and regressive soil evolution phases in the Anthropocene Manon Bajard, Jérôme Poulenard, Pierre Sabatier, Anne-Lise Develle, Charline Giguet- Covex, Jeremy Jacob, Christian Crouzet, Fernand David, Cécile Pignol, Fabien Arnaud Highlights • Lake sediment archives are used to reconstruct past soil evolution. • Erosion is quantified and the sediment geochemistry is compared to current soils. • We observed phases of greater erosion rates than soil formation rates. • These negative soil balance phases are defined as regressive pedogenesis phases. • During the Middle Ages, the erosion of increasingly deep horizons rejuvenated pedogenesis. Abstract Soils have a substantial role in the environment because they provide several ecosystem services such as food supply or carbon storage. Agricultural practices can modify soil properties and soil evolution processes, hence threatening these services. These modifications are poorly studied, and the resilience/adaptation times of soils to disruptions are unknown. Here, we study the evolution of pedogenetic processes and soil evolution phases (progressive or regressive) in response to human-induced erosion from a 4000-year lake sediment sequence (Lake La Thuile, French Alps). Erosion in this small lake catchment in the montane area is quantified from the terrigenous sediments that were trapped in the lake and compared to the soil formation rate. To access this quantification, soil processes evolution are deciphered from soil and sediment geochemistry comparison. Over the last 4000 years, first impacts on soils are recorded at approximately 1600 yr cal. BP, with the erosion of surface horizons exceeding 10 t·km− 2·yr− 1. Increasingly deep horizons were eroded with erosion accentuation during the Higher Middle Ages (1400–850 yr cal. -
Effects of Climatic Change on Soil Hydraulic Properties During
water Article Effects of Climatic Change on Soil Hydraulic Properties during the Last Interglacial Period: Two Case Studies of the Southern Chinese Loess Plateau Tieniu Wu 1,2 , Henry Lin 2, Hailin Zhang 1,*, Fei Ye 1, Yongwu Wang 1, Muxing Liu 1, Jun Yi 1 and Pei Tian 1 1 Key Laboratory for Geographical Process Analysis & Simulation, Hubei Province, Central China Normal University, Wuhan 430079, China; [email protected] (T.W.); [email protected] (F.Y.); [email protected] (Y.W.); [email protected] (M.L.); [email protected] (J.Y.); [email protected] (P.T.) 2 Department of Ecosystem Science and Management, The Pennsylvania State University, University Park, PA 16802, USA; [email protected] * Correspondence: [email protected]; Tel.: +86-27-6786-7503 Received: 16 January 2020; Accepted: 10 February 2020; Published: 12 February 2020 Abstract: The hydraulic properties of paleosols on the Chinese Loess Plateau (CLP) are closely related to agricultural production and are indicative of the environmental evolution during geological and pedogenic periods. In this study, two typical intact sequences of the first paleosol layer (S1) on the southern CLP were selected, and soil hydraulic parameters together with basic physical and chemical properties were investigated to reveal the response of soil hydraulic properties to the warm and wet climate conditions. The results show that: (1) the paleoclimate in the southern CLP during the last interglacial period showed a pattern of three warm and -
Age of Soil Organic Matter and Soil Respiration: Radiocarbon Constraints on Belowground C Dynamics
April 2000 BELOWGROUND PROCESSES AND GLOBAL CHANGE 399 Ecological Applications, 10(2), 2000, pp. 399±411 q 2000 by the Ecological Society of America AGE OF SOIL ORGANIC MATTER AND SOIL RESPIRATION: RADIOCARBON CONSTRAINTS ON BELOWGROUND C DYNAMICS SUSAN TRUMBORE Department of Earth System Science, University of California, Irvine, California 92697-3100 USA Abstract. Radiocarbon data from soil organic matter and soil respiration provide pow- erful constraints for determining carbon dynamics and thereby the magnitude and timing of soil carbon response to global change. In this paper, data from three sites representing well-drained soils in boreal, temperate, and tropical forests are used to illustrate the methods for using radiocarbon to determine the turnover times of soil organic matter and to partition soil respiration. For these sites, the average age of bulk carbon in detrital and Oh/A-horizon organic carbon ranges from 200 to 1200 yr. In each case, this mass-weighted average includes components such as relatively undecomposed leaf, root, and moss litter with much shorter turnover times, and humi®ed or mineral-associated organic matter with much longer turnover times. The average age of carbon in organic matter is greater than the average age predicted for CO2 produced by its decomposition (30, 8, and 3 yr for boreal, temperate, and tropical soil), or measured in total soil respiration (16, 3, and 1 yr). Most of the CO2 produced during decomposition is derived from relatively short-lived soil organic matter (SOM) components that do not represent a large component of the standing stock of soil organic matter. Estimates of soil carbon turnover obtained by dividing C stocks by hetero- trophic respiration ¯uxes, or from radiocarbon measurements of bulk SOM, are biased to longer time scales of C cycling. -
Interpreting, Measuring, and Modeling Soil Respiration
Biogeochemistry (2005) 73: 3–27 Ó Springer 2005 DOI 10.1007/s10533-004-5167-7 -1 Interpreting, measuring, and modeling soil respiration MICHAEL G. RYAN1,2,* and BEVERLY E. LAW3 1US Department of Agriculture-Forest Service, Rocky Mountain Research Station, 240 West Pros- pect Street, Fort Collins, CO 80526, USA; 2Affiliate Faculty, Department of Forest, Rangeland and Watershed Stewardship and Graduate Degree Program in Ecology, Colorado State University Fort Collins, CO 80523, USA; 3Department of Forest Science, Oregon State University, 328 Richardson Hall, Corvallis, OR 97331, USA; *Author for correspondence (e-mail: [email protected]) Key words: Belowground carbon allocation, Carbon cycling, Carbon dioxide, CO2, Infrared gas analyzers, Methods, Soil carbon, Terrestrial ecosystems Abstract. This paper reviews the role of soil respiration in determining ecosystem carbon balance, and the conceptual basis for measuring and modeling soil respiration. We developed it to provide background and context for this special issue on soil respiration and to synthesize the presentations and discussions at the workshop. Soil respiration is the largest component of ecosystem respiration. Because autotrophic and heterotrophic activity belowground is controlled by substrate availability, soil respiration is strongly linked to plant metabolism, photosynthesis and litterfall. This link dominates both base rates and short-term fluctuations in soil respiration and suggests many roles for soil respiration as an indicator of ecosystem metabolism. However, the strong links between above and belowground processes complicate using soil respiration to understand changes in ecosystem carbon storage. Root and associated mycorrhizal respiration produce roughly half of soil respiration, with much of the remainder derived from decomposition of recently produced root and leaf litter. -
Zinc Redistribution in a Soil Developed from Limestone During Pedogenesis C
Zinc Redistribution in a Soil Developed from Limestone During Pedogenesis C. Laveuf, Sophie Cornu, Denis Baize, Michel Hardy, Olivier Josière, Sylvain Drouin, Ary Bruand, F. Juillot To cite this version: C. Laveuf, Sophie Cornu, Denis Baize, Michel Hardy, Olivier Josière, et al.. Zinc Redistribution in a Soil Developed from Limestone During Pedogenesis. Pedosphere, Elsevier, 2009, 19 (3), pp.292-304. 10.1016/S1002-0160(09)60120-X. insu-00403877 HAL Id: insu-00403877 https://hal-insu.archives-ouvertes.fr/insu-00403877 Submitted on 21 Nov 2016 HAL is a multi-disciplinary open access L’archive ouverte pluridisciplinaire HAL, est archive for the deposit and dissemination of sci- destinée au dépôt et à la diffusion de documents entific research documents, whether they are pub- scientifiques de niveau recherche, publiés ou non, lished or not. The documents may come from émanant des établissements d’enseignement et de teaching and research institutions in France or recherche français ou étrangers, des laboratoires abroad, or from public or private research centers. publics ou privés. Zinc Redistribution in a Soil Developed from Limestone During Pedogenesis∗1 C. LAVEUF1,∗2,S.CORNU1, D. BAIZE1, M. HARDY1, O. JOSIERE1, S. DROUIN2, A. BRUAND2 and F. JUILLOT3 1INRA, UR0272 Science du Sol, Centre de recherche d’Orl´eans, 45075 Orl´eans cedex 2 (France) 2ISTO, UMR 6113, CNRS, Universit´ed’Orl´eans, 45071 Orl´eans cedex 2 (France) 3IMPMC, UMR CNRS 7590, Universit´e Paris 6 et 7, IPGC, 75252 Paris cedex 05 (France) (Received November 20, 2008; revised March 23, 2009) ABSTRACT The long-term redistribution of Zn in a naturally Zn-enriched soil during pedogenesis was quantified based on mass balance calculations. -
Measuring and Modelling Soil Carbon Stocks and Stock Changes in Livestock Production Systems Guidelines for Assessment
http://www.fao.org/partnerships/leap VERSION 1 Measuring and modelling soil carbon stocks and stock changes in livestock production systems Guidelines for assessment CA000EN/0/00.19 VERSION 1 Measuring and modelling soil carbon stocks and stock changes in livestock production systems Guidelines for assessment FOOD AND AGRICULTURE ORGANIZATION OF THE UNITED NATIONS Rome, 2019 Recommended Citation FAO. 2019. Measuring and modelling soil carbon stocks and stock changes in livestock production systems: Guidelines for assessment (Version 1). Livestock Environmental Assessment and Performance (LEAP) Partnership. Rome, FAO. 170 pp. Licence: CC BY-NC-SA 3.0 IGO. The LEAP guidelines are subject to continuous updates. Make sure to use the latest version by visiting http://www.fao.org/partnerships/leap/publications/en/ The designations employed and the presentation of material in this information product do not imply the expression of any opinion whatsoever on the part of the Food and Agriculture Organization of the United Nations (FAO) concerning the legal or development status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries. The mention of specific companies or products of manufacturers, whether or not these have been patented, does not imply that these have been endorsed or recommended by FAO in preference to others of a similar nature that are not mentioned. The views expressed in this information product are those of the author(s) and do not necessarily reflect the views or policies of FAO. ISBN 978-92-5-131408-1 © FAO, 2019 Some rights reserved. This work is made available under the Creative Commons Attribution-NonCommercial- ShareAlike 3.0 IGO licence (CC BY-NC-SA 3.0 IGO; https://creativecommons.org/licenses/by-nc-sa/3.0/igo/legalcode/legalcode). -
Simulation of Soil Organic Carbon Changes in Vertisols Under Conservation Tillage Using the Rothc Model
235 Scientia Agricola http://dx.doi.org/10.1590/1678-992X-2015-0487 Simulation of soil organic carbon changes in Vertisols under conservation tillage using the RothC model Lucila González Molina1*, Esaú del C. Moreno Pérez2, Aurelio Baéz Pérez3 1National Institute of Forestry, Agriculture and Livestock ABSTRACT: The purpose of this study was to determine the measured and simulated rates of Research/Valle de México Experimental Station, km 13,5 soil organic carbon (SOC) change in Vertisols in short-term experiments when the tillage system de la Carretera Los Reyes-Texcoco, C.P. 56250 − Texcoco, is changed from traditional tillage (TT) to conservation tillage (CT). The study was conducted in Estado de México − Mexico. plots in four locations in the state of Michoacán and two locations in the state of Guanajuato. In 2Chapingo Autonomous University, km 38,5 Carretera the SOC change simulation, the RothC-26.3 carbon model was evaluated with different C inputs México-Texcoco, C.P. 56230 − Texcoco, Estado de México to the soil (ET1-ET5). ET was the measured shoot biomass (SB) plus estimated rhizodeposition − Mexico. (RI). RI was tested at values of 10, 15, 18, 36 and 50 % total biomass (TB). The SOC changes 3National Institute of Forestry/Agriculture and Livestock were simulated with the best trial where ET3 = SB + (0.18*TB). Values for model efficiency and Research − Bajío Experimental Station, km 6,5 Carretera the coefficient of correlation were in the ranges of 0.56 to 0.75 and 0.79 to 0.92, respectively. Celaya-San Miguel de Allende, C.P. 38010 − Celaya, The average rate of SOC change, measured and simulated, in the study period was 3.0 and Guanajuato − Mexico. -
Soil Organic Carbon in a Changing World
Pedosphere 27(5): 789{791, 2017 doi:10.1016/S1002-0160(17)60489-2 ISSN 1002-0160/CN 32-1315/P ⃝c 2017 Soil Science Society of China Published by Elsevier B.V. and Science Press Preface Soil Organic Carbon in a Changing World JIA Zhongjun1, Yakov KUZYAKOV2;3, David MYROLD4 and James TIEDJE5 1State Key Laboratory of Soil and Sustainable Agriculture, Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008 (China). E-mail: [email protected] 2Agro-Technology Institute, RUDN University, Moscow 115419 (Russia). E-mail: [email protected] 3Institute of Physicochemical and Biological Problems in Soil Science, RAS, Pushchino 142290 (Russia) 4Department of Crop and Soil Science, Oregon State University, Corvallis OR 97331 (USA). E-mail: [email protected] 5Center for Microbial Ecology, Michigan State University, East Lansing MI 48824-1325 (USA). E-mail: [email protected] Soil contains more than three times as much carbon like compounds. By characterizing soil organic matter (C) as either the atmosphere or terrestrial vegetation. species using solid-state 13C cross polarization magic Soil organic C (SOC) is essentially derived from in- angle spinning (CPMAS) nuclear magnetic resonance puts of plant and animal residues, which are processed (NMR) (13C CPMAS-NMR) spectroscopy of humic by the microbiota (bacteria, archaea, protists, fungi substances and density-based fractions in a forest eco- and viruses) that dominates SOC transformation and system, Ranatunga et al. observed greater fractions of turnover in complex terrestrial environments. A tiny alkyl C, O-alkyl C, and carbohydrate functional gro- change in the SOC pool would have profound impacts ups in response to burning.