Dynamic emergy accounting of water and carbon ecosystem services: A model to simulate the impacts of land-use change

Abstract Expansion of agriculture over ecosystem areas is widely recognized as one of the most significant human alterations to the global environment over the last century. Although food and fiber production are essential ecosystem services (ES) to humankind, the clearing of forests for agricultural use is associated with changes in land cover which affect a wide range of ES at local, regional and global scales. Considering the importance of climate change, freshwater scarcity, soil erosion and other environmental issues, this paper aims to simulate the impact of land-use change on the ecosystem services related to water and carbon biogeochemical processes. The system under study is the Taquarizinho river basin, located in the eastern region of Mato Grosso do Sul State, Brazil, inserted in the upland borders of one of the largest wetland systems of the world, the Pantanal. Formerly occupied by Brazilian savannah (Cerrado), more than half of Taquarizinho watershed was converted both to agriculture and pasture lands since the 1960s. In order to quantify the impact of land-use change on ES provided by Taquarizinho over the years, this paper introduces the hydro-carbon model, which dynamically represents ecosystem services related to water and carbon cycles, such as canal discharge, groundwater recharge, evapotranspiration, biomass carbon sequestration, litter carbon sequestration, and soil carbon sequestration. The hydro-carbon model uses emergy for estimating the monetary value of ecosystem services provided by the river basin under different land-use scenarios. In this paper, extreme scenarios represent typical land-use types in Taquarizinho basin: native savanna (NS), agroforestry systems (AF), conventional tillage agriculture (CT), no-tillage multiple cropping agriculture (NT), degraded pastures (DP), and pastures under improved management (IP). Results in this paper reveal a hierarchy related to water and carbon ES provision, in descending order: native savanna (247 EM$ ha−1 y−1), agroforestry system (204 EM$ ha−1 y−1), pastures under improved management (180 EM$ ha−1 y−1), no-tillage multiple cropping agriculture (160 EM$ ha−1 y−1), degraded pastures (104 EM$ ha−1 y−1) and conventional tillage agriculture (75 EM$ ha−1 y−1).

[1]  Donald L. Tennant Instream Flow Regimens for Fish, Wildlife, Recreation and Related Environmental Resources , 1976 .

[2]  C.Y. Jim,et al.  Ecosystem services and valuation of urban forests in China , 2009 .

[3]  B. Bakshi,et al.  Promise and problems of emergy analysis , 2004 .

[4]  J. Tenhunen,et al.  On the relationship of NDVI with leaf area index in a deciduous forest site , 2005 .

[5]  S. Polasky,et al.  Agricultural sustainability and intensive production practices , 2002, Nature.

[6]  Brian G. Wolff,et al.  Forecasting Agriculturally Driven Global Environmental Change , 2001, Science.

[7]  E. Lambin,et al.  INAUGURAL ARTICLE by a Recently Elected Academy Member:Global land use change, economic globalization, and the looming land scarcity , 2011 .

[8]  Rafael Nóra Tannus Funcionalidade e sazonalidade sobre cerrano e sobre ecótono floresta-cerrado: uma investigação com dados micrometeorológicos de energia e CO2 , 2004 .

[9]  Tony Prato Selection and evaluation of projects to conserve ecosystem services , 2007 .

[10]  J. Levine Greenhouse Gas Contributions from Deforestation in Brazilian Amazonia , 1991 .

[11]  Millenium Ecosystem Assessment Ecosystems and human well-being: synthesis , 2005 .

[12]  Mark T. Brown,et al.  Dynamic emergy accounting for assessing the environmental benefits of subtropical wetland stormwater management systems , 2006 .

[13]  P. Girard,et al.  River–groundwater interactions in the Brazilian Pantanal. The case of the Cuiabá River , 2003 .

[14]  H. K. Chang,et al.  Stable isotopes (2H, 18O and 13C) in groundwaters from the northwestern portion of the Guarani Aquifer System (Brazil) , 2010 .

[15]  Howard T. Odum,et al.  Environmental Accounting: Emergy and Environmental Decision Making , 1995 .

[16]  R. Lal,et al.  Soil carbon storage and sequestration potential in the Cerrado Region of Brazil. , 2006 .

[17]  M. L. L. Assad,et al.  Estoques de carbono em solos sob diferentes fitofisionomias de cerrados , 1996 .

[18]  Interface ecosystems with an oil spill in a Venezuelan tropical savannah , 1997 .

[19]  Claire Chenu,et al.  Relationship of soil organic matter dynamics to physical protection and tillage , 2000 .

[20]  M. Altieri The ecological role of biodiversity in agroecosystems , 1999 .

[21]  C. D. Gouvello,et al.  Brazil low-carbon country case study , 2010 .

[22]  W. Parton,et al.  Agricultural intensification and ecosystem properties. , 1997, Science.

[23]  Enrique Ortega,et al.  Ecosystem services and biogeochemical cycles on a global scale: valuation of water, carbon and nitrogen processes , 2011 .

[24]  W. Goedert Solos dos Cerrados : tecnologias e estratégias de manejo , 1985 .

[25]  T. Ricketts,et al.  Ecosystem services and dis-services to agriculture , 2007 .

[26]  Prem S. Bindraban,et al.  Changes in organic carbon stocks upon land use conversion in the Brazilian Cerrado: a review. , 2010 .

[27]  Rafael Rosolem,et al.  Measurements of CO2 exchange over a woodland savanna (Cerrado Sensu stricto) in southeast Brasil , 2002 .

[28]  Howard T. Odum,et al.  The Energetic Basis for Valuation of Ecosystem Services , 2000, Ecosystems.