2019
DOI: 10.1016/j.geoderma.2018.09.045
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Changes in soil carbon stocks after land-use change from native vegetation to pastures in the Atlantic forest region of Brazil

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Cited by 41 publications
(19 citation statements)
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“…The results of TOC and Cstock demonstrate the negative impact of incorrect pasture management, in which little vegetation cover limits the SOM entry into the soil (Santos et al, 2019;Segnini et al, 2019;Lopes et al, 2020). Segnini et al (2019) assessed C loss in pastures under different grazing intensities and reported low TOC contents in degraded pasture areas compared to natural vegetation areas.…”
Section: Resultsmentioning
confidence: 97%
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“…The results of TOC and Cstock demonstrate the negative impact of incorrect pasture management, in which little vegetation cover limits the SOM entry into the soil (Santos et al, 2019;Segnini et al, 2019;Lopes et al, 2020). Segnini et al (2019) assessed C loss in pastures under different grazing intensities and reported low TOC contents in degraded pasture areas compared to natural vegetation areas.…”
Section: Resultsmentioning
confidence: 97%
“…Segnini et al (2019) assessed C loss in pastures under different grazing intensities and reported low TOC contents in degraded pasture areas compared to natural vegetation areas. Pasture systems can benefit C inputs in the system when properly managed and, consequently, increase Cstock (Salton et al, 2008;Santos et al, 2019;Falcão et al, 2020), favoring the quality of the edaphic environment and contributing to reducing greenhouse gas emissions (Koven et al, 2017).…”
Section: Resultsmentioning
confidence: 99%
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“…Outros sistemas como as pastagens, quando bem manejadas, são destaques em acúmulos de C e estruturação do solo, principalmente em camadas subsuperficiais, pela ação de suas raízes que, ao se decomporem, adicionam quantidades significativas de MOS (SALTON et al, 2008;SANTOS et al, 2019).…”
Section: Introductionunclassified
“…Until now, many investigations have evaluated the changes of SOC after the conversion of wetlands to agriculture (Wang, Wang, Feng, Guo, & Chen, 2014) and forestry activities (Ramesh et al, 2019), pastures (Steinman, Conklin, Bohlen, & Uzarski, 2003), aquaculture (Yang et al, 2018), and urbanization development (Pouyat, Yesilonis, & Nowak, 2006), but the depths of soil sampling in these studies were less than 30 cm (e.g., Chen, Arrouays, Angers, Martin, & Walter, 2019; Xu et al, 2017). Many of these studies have just compared SOC contents, fractions, aggregate‐associated organic C and stocks (e.g., dos Santos et al, 2019; Huo et al, 2018; Zhong et al, 2019; Zhu et al, 2020) rather than SOC sources, stability and the mechanisms controlling SOC turnover between wetlands and other land use types. For example, Huo et al (2018) found that dissolved organic carbon, microbial biomass carbon, readily oxidized carbon and readily mineralized carbon in a paddy field were lower than those in natural wetland by 13.8, 35.1, 59.0, and 17.9%, respectively.…”
Section: Introductionmentioning
confidence: 99%