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Frontiers of Earth Science

ISSN 2095-0195

ISSN 2095-0209(Online)

CN 11-5982/P

邮发代号 80-963

2019 Impact Factor: 1.62

Frontiers of Earth Science  2018, Vol. 12 Issue (2): 339-348   https://doi.org/10.1007/s11707-018-0680-5
  本期目录
Effect of reclamation on soil organic carbon pools in coastal areas of eastern China
Jianguo LI1, Wenhui YANG1, Qiang LI1, Lijie PU2,3(), Yan XU2, Zhongqi ZHANG1, Lili LIU1
1. School of Geography, Geomatics and Planning, Jiangsu Normal University, Xuzhou 221116, China
2. School of Geographic and Oceanographic Sciences, Nanjing University, Nanjing 210023, China
3. Key Laboratory of Coastal Zone Exploitation and Protection, Ministry of Land and Resources, Nanjing 210023, China
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Abstract

The coastal wetlands of eastern China form one of the most important carbon sinks in the world. However, reclamation can significantly alter the soil carbon pool dynamics in these areas. In this study, a chronosequence was constructed for four reclamation zones in Rudong County, Jiangsu Province, eastern China (reclaimed in 1951, 1974, 1982, and 2007) and a reference salt marsh to identify both the process of soil organic carbon (SOC) evolution, as well as the effect of cropping and soil properties on SOC with time after reclamation. The results show that whereas soil nutrient elements and SOC increased after reclamation, the electrical conductivity of the saturated soil extract (ECe), pH, and bulk density decreased within 62 years following reclamation and agricultural amendment. In general, the soil’s chemical properties remarkably improved and SOC increased significantly for approximately 30 years after reclamation. Reclamation for agriculture (rice and cotton) significantly increased the soil organic carbon density (SOCD) in the top 60 cm, especially in the top 0–30 cm. However, whereas the highest concentration of SOCD in rice-growing areas was in the top 0–20 cm of the soil profile, it was greater at a 20–60 cm depth in cotton-growing areas. Reclamation also significantly increased heavy fraction organic carbon (HFOC) levels in the 0–30 cm layer, thereby enhancing the stability of the soil carbon pool. SOC can thus increase significantly over a long time period after coastal reclamation, especially in areas of cultivation, where coastal SOC pools in eastern China tend to be more stable.

Key wordssoil organic carbon (SOC)    reclamation time    land use    coastal wetlands    heavy fraction organic carbon (HFOC)    light fraction organic carbon (LFOC)
收稿日期: 2016-11-07      出版日期: 2018-05-09
Corresponding Author(s): Lijie PU   
 引用本文:   
. [J]. Frontiers of Earth Science, 2018, 12(2): 339-348.
Jianguo LI, Wenhui YANG, Qiang LI, Lijie PU, Yan XU, Zhongqi ZHANG, Lili LIU. Effect of reclamation on soil organic carbon pools in coastal areas of eastern China. Front. Earth Sci., 2018, 12(2): 339-348.
 链接本文:  
https://academic.hep.com.cn/fesci/CN/10.1007/s11707-018-0680-5
https://academic.hep.com.cn/fesci/CN/Y2018/V12/I2/339
Fig.1  
Properties 1951
(n=14)
1974
(n=14)
1982
(n=10)
2002
(n=10)
Salt marsh
(n=8)
ECe/(dS·m1) 2.04a 6.72a 11.73a 50.08b 48.78b
pH 8.26a 8.22a 8.48b 8.70c 8.63c
Sand silt clay 15:75:10 31:64:5 31:63:6 44:52:04 42:53:05
Bulk density/(kg·m3) 1640a 1640a 1570c 1700b 1720b
TN/% 0.07a 0.05b 0.05b 0.03c 0.02c
TP/% 0.07a 0.07a 0.06ab 0.06b 0.06b
TK/% 11.52a 12.57a 12.15a 12.86a 13.16a
OM/% 0.75a 0.84a 0.72a 0.45b 0.45b
Ti/Zr 14.08a 14.37a 14.37a 14.81a 15.19a
Tab.1  
Fig.2  
Year SOC/(g·kg−1)
  0–10 cm 10–20 cm 20–30 cm 30–40 cm 40–60 cm
1951
(n=6)
H 2.9±0.06a 3.08±0.04a 2.6±0.1a 1.97±0.08a 1.69±0.08a
L 1.03±0.23A 0.88±0.23A 0.44±0.09A 0.33±0.24A 0.14±0.1A
L:H 0.26:0.74 0.22:0.78 0.15:0.85 0.15:0.85 0.08:0.92
1974
(n=6)
H 3.92±0.25a 2.04±0.03a 1.84±0.09a 1.58±0.1a 1.32±0.03a
L 0.99±0.1A 0.74±0.44A 0.4±0.28A 0.23±0.4A 0.15±0.14A
L:H 0.2:0.80 0.26:0.74 0.18:0.82 0.13:0.87 0.11:0.89
1982
(n=6)
H 2.57±0.06a 2.15±0.15a 1.65±0.01a 1.88±0.08a 2.02±0.03a
L 0.66±0.16A 0.73±0.28A 0.47±0.06A 0.35±0.26A 0.12±0.14B
L:H 0.20:0.80 0.25:0.75 0.22:0.78 0.16:0.84 0.06:0.94
2002
(n=6)
H 0.96±0.05b 1.08±0.03b 1.03±0.08b 1.14±0.1a 0.98±0.007a
L 0.41±1.48A 0.19±0.02A 0.1±0.15A 0.13±0.2A 0.09±0.09A
L:H 0.30:0.70 0.15:0.85 0.09:0.91 0.11:0.89 0.09:0.91
Salt
Marsh
(n=6)
H 1.15±0.03b 0.78±0.12b 1.33±0.02b 1.29±0.06a 1.84±0.16a
L 0.17±0.17B 0.14±0.09A 0.1±0.06A 0.08±0.04A 0.02±0.03B
L:H 0.13:0.87 0.15:0.85 0.07:0.93 0.05:0.95 0.01:0.99
Tab.2  
Fig.3  
Moisture ECe %Clay TN AN TP AP TK CEC pH
SOC
(n=112)
0.09 –0.30 0.01 ?0.74** ?0.52** ?0.68** ?0.45** –0.17 –0.12 ?–0.60**
Tab.3  
Fig.4  
Fig.5  
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