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  2. College of Bioresources and Agriculture / 生物資源暨農學院
  3. Forestry and Resource Conservation / 森林環境暨資源學系
  4. Soil organic C stabilization and thresholds in C saturation
 
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Soil organic C stabilization and thresholds in C saturation

Journal
Soil Biology and Biochemistry
Journal Volume
41
Journal Issue
10
Pages
2100-2104
Date Issued
2009
Author(s)
Kimetu, J.M.
Lehmann, J.
Kinyangi, J.M.
CHIH-HSIN CHENG  
Thies, J.
Mugendi, D.N.
Pell, A.
DOI
10.1016/j.soilbio.2009.07.022
URI
http://www.scopus.com/inward/record.url?eid=2-s2.0-70249120304&partnerID=MN8TOARS
http://scholars.lib.ntu.edu.tw/handle/123456789/351000
Abstract
When building soil organic matter (SOM) contents in agricultural production systems, stabilization of both pre-existing as well as added C is important. A laboratory mineralization experiment was conducted over 374 days to evaluate the effect of pre-existing SOM on soil C mineralization after addition of organic matter (OM) using sugar cane. The SOM gradient used here stretched from 21 to 106 g C kg-1 soil and was a result of different periods of continuous cultivation of 5, 20, 35 and 105 years in comparison to a forest soil. The rate of organic C mineralization was found to be dependent on the status of pre-existing soil organic C (SOC). Highly degraded soil which had been under continuous cultivation for 35 years and more showed the highest rate of C mineralization per unit SOC (117.9 mg C g-1 C) while forest soil had the lowest amount of C mineralized per unit SOC (73.5 mg C g-1 C). Forest soil had the highest amount of increased C mineralization as a result of organic matter (OM) additions (8.0 mg C g-1 soil) followed by the highly degraded soil that had been under cultivation for 105 years (5.5 mg C g-1 soil). Additional mineralized C as a function of time after forest conversion declined progressively within the first 20 years of continuous soil use. Soil which had been under continuous cultivation for 20 years had the lowest amount of additional mineralized C (4.0 mg C g-1 soil). SOM stabilization efficiency in the studied soils appears to be highest with intermediate cultivation history of about 20 years. These soils that have been recently converted to cultivation also appear to have a greater ability to stabilize added OM than the most degraded soils investigated in this study. It is thus advisable to provide intervention strategies to reverse SOM decline for farming communities at an intermediate stage before the soils are highly depleted of SOC. © 2009 Elsevier Ltd. All rights reserved.
Subjects
Carbon saturation; SOC stabilization; Soil degradation
SDGs

[SDGs]SDG2

Other Subjects
Agricultural production system; C mineralization; Carbon saturation; Continuous cultivation; Degraded soils; Forest conversion; Forest soils; Function of time; Intermediate stage; Intervention strategy; Organic matter; Per unit; SOC stabilization; Soil degradation; Soil organic C; Soil organic matters; Soil use; Biogeochemistry; Biological materials; Cultivation; Degradation; Mineralogy; Organic compounds; Programmable logic controllers; Stabilization; Strength of materials; Sugar (sucrose); Sugar cane; Sugars; Soils; agricultural production; agricultural soil; comparative study; forest soil; mineralization; soil carbon; soil degradation; soil organic matter; sugar cane; Saccharum
Type
journal article

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