Soil Carbon Change Due to Land Conversion to Grassland in a Semi-Arid Environment

A 5-year study evaluated the change in the quantity of soil total C (STC), soil organic C (SOC), and soil inorganic C (SIC) stored in the surface 60 cm of the soil profile on two adjacent blocks of land with a long-term history of cropping (CH) or undisturbed grassland (NH) on similar soil types bet...

Full description

Bibliographic Details
Main Authors: Gayatri Yellajosula, Larry Cihacek, Tim Faller, Christopher Schauer
Format: Article
Language:English
Published: MDPI AG 2020-07-01
Series:Soil Systems
Subjects:
Online Access:https://www.mdpi.com/2571-8789/4/3/43
_version_ 1797562269579608064
author Gayatri Yellajosula
Larry Cihacek
Tim Faller
Christopher Schauer
author_facet Gayatri Yellajosula
Larry Cihacek
Tim Faller
Christopher Schauer
author_sort Gayatri Yellajosula
collection DOAJ
description A 5-year study evaluated the change in the quantity of soil total C (STC), soil organic C (SOC), and soil inorganic C (SIC) stored in the surface 60 cm of the soil profile on two adjacent blocks of land with a long-term history of cropping (CH) or undisturbed grassland (NH) on similar soil types between 1999 and 2004. The NH area was tilled and a grass-legume species mix was seeded into plots on both the NH and the CH areas. Selected plots of restored grass were established so they could be grazed (GG) by livestock while other plots were left ungrazed (UG). Original undisturbed (and ungrazed) grassland plots within the NH area were used as a control treatment. Initially, STC and SOC in CH were lower than NH when compared under the semi-arid environmental conditions found in southwestern North Dakota. Over the study period, the undisturbed grass control plots had increases in STC and SOC levels in the soil profile of 3.90 kg·m<sup>−2</sup> and 3.34 kg·m<sup>−2</sup>, respectively. Restored grass on the NH area with grazing showed increases in STC and SOC values of 2.11 and 1.26 kg·m<sup>−2</sup>, respectively, while without grazing, profile STC and SOC had values of 3.80 and 3.28 kg·m<sup>−2</sup>, respectively. Restored grass on the CH area showed increases in profile STC and SOC values of 0.55 and 1.96 kg·m<sup>−2</sup>, respectively, for the grazed plots and 0.78 and 2.11 kg·m<sup>−2</sup>, respectively, when left ungrazed. Soil inorganic C, though present in the soils, did not significantly change during the study. The lower C accumulation in the CH plots may be due to a lag time in the establishment of mycorrhizal associations with the seeded species, the inoculums of which were already present in the NH soils. Changes in STC were likely due to changes in water relationships in the soil profile where management changes affected water infiltration and its movement causing leaching of SIC below the 60 cm depth evaluated. Soils under undisturbed grassland continue to accumulate carbon while soils of the disturbed grassland or cropped prior to re-establishing grass showed losses that occurred due to either accumulating C at a lower rate or perhaps to C loss during the initial establishment period (1–2 years).
first_indexed 2024-03-10T18:25:53Z
format Article
id doaj.art-7e49fc8ed4d94e66880214aa974dce20
institution Directory Open Access Journal
issn 2571-8789
language English
last_indexed 2024-03-10T18:25:53Z
publishDate 2020-07-01
publisher MDPI AG
record_format Article
series Soil Systems
spelling doaj.art-7e49fc8ed4d94e66880214aa974dce202023-11-20T07:00:11ZengMDPI AGSoil Systems2571-87892020-07-01434310.3390/soilsystems4030043Soil Carbon Change Due to Land Conversion to Grassland in a Semi-Arid EnvironmentGayatri Yellajosula0Larry Cihacek1Tim Faller2Christopher Schauer3Soil Science Department, School of Natural Resource Sciences, North Dakota State University, Fargo, ND 58108, USASoil Science Department, School of Natural Resource Sciences, North Dakota State University, Fargo, ND 58108, USAHettinger Research Extension Center, North Dakota State University, Hettinger, ND 58639, USAHettinger Research Extension Center, North Dakota State University, Hettinger, ND 58639, USAA 5-year study evaluated the change in the quantity of soil total C (STC), soil organic C (SOC), and soil inorganic C (SIC) stored in the surface 60 cm of the soil profile on two adjacent blocks of land with a long-term history of cropping (CH) or undisturbed grassland (NH) on similar soil types between 1999 and 2004. The NH area was tilled and a grass-legume species mix was seeded into plots on both the NH and the CH areas. Selected plots of restored grass were established so they could be grazed (GG) by livestock while other plots were left ungrazed (UG). Original undisturbed (and ungrazed) grassland plots within the NH area were used as a control treatment. Initially, STC and SOC in CH were lower than NH when compared under the semi-arid environmental conditions found in southwestern North Dakota. Over the study period, the undisturbed grass control plots had increases in STC and SOC levels in the soil profile of 3.90 kg·m<sup>−2</sup> and 3.34 kg·m<sup>−2</sup>, respectively. Restored grass on the NH area with grazing showed increases in STC and SOC values of 2.11 and 1.26 kg·m<sup>−2</sup>, respectively, while without grazing, profile STC and SOC had values of 3.80 and 3.28 kg·m<sup>−2</sup>, respectively. Restored grass on the CH area showed increases in profile STC and SOC values of 0.55 and 1.96 kg·m<sup>−2</sup>, respectively, for the grazed plots and 0.78 and 2.11 kg·m<sup>−2</sup>, respectively, when left ungrazed. Soil inorganic C, though present in the soils, did not significantly change during the study. The lower C accumulation in the CH plots may be due to a lag time in the establishment of mycorrhizal associations with the seeded species, the inoculums of which were already present in the NH soils. Changes in STC were likely due to changes in water relationships in the soil profile where management changes affected water infiltration and its movement causing leaching of SIC below the 60 cm depth evaluated. Soils under undisturbed grassland continue to accumulate carbon while soils of the disturbed grassland or cropped prior to re-establishing grass showed losses that occurred due to either accumulating C at a lower rate or perhaps to C loss during the initial establishment period (1–2 years).https://www.mdpi.com/2571-8789/4/3/43soil carbongrassland restorationcropped land historygrassland historysoil organic carbonsoil inorganic carbon
spellingShingle Gayatri Yellajosula
Larry Cihacek
Tim Faller
Christopher Schauer
Soil Carbon Change Due to Land Conversion to Grassland in a Semi-Arid Environment
Soil Systems
soil carbon
grassland restoration
cropped land history
grassland history
soil organic carbon
soil inorganic carbon
title Soil Carbon Change Due to Land Conversion to Grassland in a Semi-Arid Environment
title_full Soil Carbon Change Due to Land Conversion to Grassland in a Semi-Arid Environment
title_fullStr Soil Carbon Change Due to Land Conversion to Grassland in a Semi-Arid Environment
title_full_unstemmed Soil Carbon Change Due to Land Conversion to Grassland in a Semi-Arid Environment
title_short Soil Carbon Change Due to Land Conversion to Grassland in a Semi-Arid Environment
title_sort soil carbon change due to land conversion to grassland in a semi arid environment
topic soil carbon
grassland restoration
cropped land history
grassland history
soil organic carbon
soil inorganic carbon
url https://www.mdpi.com/2571-8789/4/3/43
work_keys_str_mv AT gayatriyellajosula soilcarbonchangeduetolandconversiontograsslandinasemiaridenvironment
AT larrycihacek soilcarbonchangeduetolandconversiontograsslandinasemiaridenvironment
AT timfaller soilcarbonchangeduetolandconversiontograsslandinasemiaridenvironment
AT christopherschauer soilcarbonchangeduetolandconversiontograsslandinasemiaridenvironment