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ECOSER PROJECT: TOWARD A BETTER UNDERSTANDING OF THE ECOSER PROJECT: TOWARD A BETTER UNDERSTANDING OF THE MECHANISMS OF CARBON STABILIZATION IN AGRICULTURAL SOILS MECHANISMS OF CARBON STABILIZATION IN AGRICULTURAL SOILS AMENDED WITH MUNICIPAL ORGANIC WASTES AMENDED WITH MUNICIPAL ORGANIC WASTES OBJECTIVES OBJECTIVES The main objective of the ECOSER project is to develop a better understanding of the processes controlling the transformation and The main objective of the ECOSER project is to develop a better understanding of the processes controlling the transformation and stabilization of organic matter in agricultural soils amended with municipal organic wastes, and to evaluate the agricultural and stabilization of organic matter in agricultural soils amended with municipal organic wastes, and to evaluate the agricultural and environmental implications related to plant nutrient supply and C sequestration. environmental implications related to plant nutrient supply and C sequestration. C. Plaza, R. Sanz, P. J. Hernáiz, J. C. García-Gil, P. A. C. Plaza, R. Sanz, P. J. Hernáiz, J. C. García-Gil, P. A. Soler-Rovira, J. M. Fernández, D. Hernández, I. Haller, and Soler-Rovira, J. M. Fernández, D. Hernández, I. Haller, and A. Polo A. Polo METHODOLOGY METHODOLOGY In October, 2008, we started a field plot experiment at “La Poveda” experimental farm (Center of Environmental Sciences, Spanish Research In October, 2008, we started a field plot experiment at “La Poveda” experimental farm (Center of Environmental Sciences, Spanish Research Council, Spanish acronym CCMA-CSIC) located in Arganda del Rey (Madrid, Spain). The experiment was set up as a randomized complete block Council, Spanish acronym CCMA-CSIC) located in Arganda del Rey (Madrid, Spain). The experiment was set up as a randomized complete block design with four replicates in a split plot treatment arrangement. The main plot treatments are (1) an unamended control, (2) a mineral design with four replicates in a split plot treatment arrangement. The main plot treatments are (1) an unamended control, (2) a mineral fertilization, and (3) municipal solid waste compost, (4) composted sewage sludge, and (5) thermally-dried sewage sludge applied at a rate fertilization, and (3) municipal solid waste compost, (4) composted sewage sludge, and (5) thermally-dried sewage sludge applied at a rate of 30 t ha of 30 t ha -1 -1 . The subplot treatments are (1) only one application of organic amendment made at the beginning of the experiment and (2) . The subplot treatments are (1) only one application of organic amendment made at the beginning of the experiment and (2) annually consecutive additions. Physical fractionation techniques based on density and size characteristics to divide organic matter annually consecutive additions. Physical fractionation techniques based on density and size characteristics to divide organic matter according to location in soil (organic particles material freely located between and within soil macroaggregates, fine organic particles according to location in soil (organic particles material freely located between and within soil macroaggregates, fine organic particles protected within stable microaggregates, and silt- and clay-associated organic matter) will be combined with advanced physicochemical, protected within stable microaggregates, and silt- and clay-associated organic matter) will be combined with advanced physicochemical, ACKNOWLEDGMENTS ACKNOWLEDGMENTS This project is being funded by the Directorate-General for Universities and Research of the Autonomous Community of Madrid (DGUI-CAM) and This project is being funded by the Directorate-General for Universities and Research of the Autonomous Community of Madrid (DGUI-CAM) and the Spanish Research Council (CSIC) through the program “Grants for Creation and Consolidation of CSIC Research Groups in the CAM” (CCG08- the Spanish Research Council (CSIC) through the program “Grants for Creation and Consolidation of CSIC Research Groups in the CAM” (CCG08- CSIC/AMB-3439). CSIC/AMB-3439). Instituto de Ciencias Agrarias, Centro de Ciencias Medioambientales, Consejo Instituto de Ciencias Agrarias, Centro de Ciencias Medioambientales, Consejo Superior de Investigaciones Científicas, Serrano 115 dpdo., 28006 Madrid, Superior de Investigaciones Científicas, Serrano 115 dpdo., 28006 Madrid, Spain Spain STATE-OF-THE-ART STATE-OF-THE-ART Land application of municipal organic wastes, especially to organically-depleted agricultural soils, is believed to be an efficient Land application of municipal organic wastes, especially to organically-depleted agricultural soils, is believed to be an efficient practice for improving soil quality and crop production, while reducing the amount of waste to be disposed of in landfills or burnt in practice for improving soil quality and crop production, while reducing the amount of waste to be disposed of in landfills or burnt in incineration plants, enhancing C sequestration, and thus helping head-off the global warming. According to current concepts, the incineration plants, enhancing C sequestration, and thus helping head-off the global warming. According to current concepts, the biogeochemical pathways responsible for exogenous organic matter stabilization in soil include (a) selective preservation and formation of biogeochemical pathways responsible for exogenous organic matter stabilization in soil include (a) selective preservation and formation of recalcitrant organic compounds (biochemical protection), (b) occlusion within soil aggregates (physical protection), and (c) association recalcitrant organic compounds (biochemical protection), (b) occlusion within soil aggregates (physical protection), and (c) association with mineral surfaces (chemical protection). To date, however, how these protective mechanisms act and interact in soils amended with with mineral surfaces (chemical protection). To date, however, how these protective mechanisms act and interact in soils amended with municipal organic wastes remains largely unknown. municipal organic wastes remains largely unknown. THERMALLY-DRIED SEWAGE SLUDGE (TS) COMPOSTED SEWAGE SLUDGE (CS) MUNICIPAL SOLID WASTE COMPOST (MC) C ontrol (unam ended) M ineral fertilization 30 tha -1 y -1 ofM C applied the firstyearonly orevery year 30 tha -1 y -1 ofC S applied the firstyearonly orevery year 30 tha -1 y -1 ofTS applied the firstyearonly orevery year U nam ended plots 2 m 44 m 3 m 2 m 32 m 15 m 6.9 m 1.2 m

ECOSER PROJECT: TOWARD A BETTER UNDERSTANDING OF THE MECHANISMS OF CARBON STABILIZATION IN AGRICULTURAL SOILS AMENDED WITH MUNICIPAL ORGANIC WASTES OBJECTIVES

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Page 1: ECOSER PROJECT: TOWARD A BETTER UNDERSTANDING OF THE MECHANISMS OF CARBON STABILIZATION IN AGRICULTURAL SOILS AMENDED WITH MUNICIPAL ORGANIC WASTES OBJECTIVES

ECOSER PROJECT: TOWARD A BETTER UNDERSTANDING OF THE ECOSER PROJECT: TOWARD A BETTER UNDERSTANDING OF THE MECHANISMS OF CARBON STABILIZATION IN AGRICULTURAL SOILS MECHANISMS OF CARBON STABILIZATION IN AGRICULTURAL SOILS

AMENDED WITH MUNICIPAL ORGANIC WASTESAMENDED WITH MUNICIPAL ORGANIC WASTES

OBJECTIVESOBJECTIVES

The main objective of the ECOSER project is to develop a better understanding of the processes controlling the transformation and stabilization of organic matter in The main objective of the ECOSER project is to develop a better understanding of the processes controlling the transformation and stabilization of organic matter in agricultural soils amended with municipal organic wastes, and to evaluate the agricultural and environmental implications related to plant nutrient supply and C agricultural soils amended with municipal organic wastes, and to evaluate the agricultural and environmental implications related to plant nutrient supply and C sequestration. sequestration.

C. Plaza, R. Sanz, P. J. Hernáiz, J. C. García-Gil, P. A. Soler-Rovira, J. M. C. Plaza, R. Sanz, P. J. Hernáiz, J. C. García-Gil, P. A. Soler-Rovira, J. M. Fernández, D. Hernández, I. Haller, and A. PoloFernández, D. Hernández, I. Haller, and A. Polo

METHODOLOGYMETHODOLOGY

In October, 2008, we started a field plot experiment at “La Poveda” experimental farm (Center of Environmental Sciences, Spanish Research Council, Spanish acronym In October, 2008, we started a field plot experiment at “La Poveda” experimental farm (Center of Environmental Sciences, Spanish Research Council, Spanish acronym CCMA-CSIC) located in Arganda del Rey (Madrid, Spain). The experiment was set up as a randomized complete block design with four replicates in a split plot treatment CCMA-CSIC) located in Arganda del Rey (Madrid, Spain). The experiment was set up as a randomized complete block design with four replicates in a split plot treatment arrangement. The main plot treatments are (1) an unamended control, (2) a mineral fertilization, and (3) municipal solid waste compost, (4) composted sewage sludge, and (5) arrangement. The main plot treatments are (1) an unamended control, (2) a mineral fertilization, and (3) municipal solid waste compost, (4) composted sewage sludge, and (5) thermally-dried sewage sludge applied at a rate of 30 t hathermally-dried sewage sludge applied at a rate of 30 t ha -1-1. The subplot treatments are (1) only one application of organic amendment made at the beginning of the . The subplot treatments are (1) only one application of organic amendment made at the beginning of the experiment and (2) annually consecutive additions. Physical fractionation techniques based on density and size characteristics to divide organic matter according to location experiment and (2) annually consecutive additions. Physical fractionation techniques based on density and size characteristics to divide organic matter according to location in soil (organic particles material freely located between and within soil macroaggregates, fine organic particles protected within stable microaggregates, and silt- and clay-in soil (organic particles material freely located between and within soil macroaggregates, fine organic particles protected within stable microaggregates, and silt- and clay-associated organic matter) will be combined with advanced physicochemical, chemical, isotopic, microbiological, and modeling approaches.associated organic matter) will be combined with advanced physicochemical, chemical, isotopic, microbiological, and modeling approaches.

ACKNOWLEDGMENTSACKNOWLEDGMENTS

This project is being funded by the Directorate-General for Universities and Research of the Autonomous Community of Madrid (DGUI-CAM) and the Spanish Research This project is being funded by the Directorate-General for Universities and Research of the Autonomous Community of Madrid (DGUI-CAM) and the Spanish Research Council (CSIC) through the program “Grants for Creation and Consolidation of CSIC Research Groups in the CAM” (CCG08-CSIC/AMB-3439).Council (CSIC) through the program “Grants for Creation and Consolidation of CSIC Research Groups in the CAM” (CCG08-CSIC/AMB-3439).

Instituto de Ciencias Agrarias, Centro de Ciencias Medioambientales, Consejo Superior de Instituto de Ciencias Agrarias, Centro de Ciencias Medioambientales, Consejo Superior de Investigaciones Científicas, Serrano 115 dpdo., 28006 Madrid, SpainInvestigaciones Científicas, Serrano 115 dpdo., 28006 Madrid, Spain

STATE-OF-THE-ART STATE-OF-THE-ART

Land application of municipal organic wastes, especially to organically-depleted agricultural soils, is believed to be an efficient practice for improving soil quality and crop Land application of municipal organic wastes, especially to organically-depleted agricultural soils, is believed to be an efficient practice for improving soil quality and crop production, while reducing the amount of waste to be disposed of in landfills or burnt in incineration plants, enhancing C sequestration, and thus helping head-off the global production, while reducing the amount of waste to be disposed of in landfills or burnt in incineration plants, enhancing C sequestration, and thus helping head-off the global warming. According to current concepts, the biogeochemical pathways responsible for exogenous organic matter stabilization in soil include (a) selective preservation and warming. According to current concepts, the biogeochemical pathways responsible for exogenous organic matter stabilization in soil include (a) selective preservation and formation of recalcitrant organic compounds (biochemical protection), (b) occlusion within soil aggregates (physical protection), and (c) association with mineral surfaces formation of recalcitrant organic compounds (biochemical protection), (b) occlusion within soil aggregates (physical protection), and (c) association with mineral surfaces (chemical protection). To date, however, how these protective mechanisms act and interact in soils amended with municipal organic wastes remains largely unknown.(chemical protection). To date, however, how these protective mechanisms act and interact in soils amended with municipal organic wastes remains largely unknown.

THERMALLY-DRIED SEWAGE SLUDGE (TS)

COMPOSTED SEWAGE SLUDGE (CS)

MUNICIPAL SOLID WASTE COMPOST (MC)

Control (unamended)

Mineral fertilization

30 t ha-1 y-1 of MC applied the first year only or every year

30 t ha-1 y-1 of CS applied the first year only or every year 30 t ha-1 y-1 of TS applied the first year only or every year

Unamended plots

2 m

44 m

3 m 2 m

32 m

15 m

6.9

m

1.2

m