001     840436
005     20210129231832.0
024 7 _ |a 10.1016/j.scitotenv.2017.07.167
|2 doi
024 7 _ |a 0048-9697
|2 ISSN
024 7 _ |a 1879-1026
|2 ISSN
024 7 _ |a pmid:28763653
|2 pmid
024 7 _ |a WOS:000410352900061
|2 WOS
024 7 _ |a altmetric:23376067
|2 altmetric
037 _ _ |a FZJ-2017-07953
082 _ _ |a 333.7
100 1 _ |a Wang, Xiaoguo
|0 P:(DE-HGF)0
|b 0
245 _ _ |a Land use change effects on ecosystem carbon budget in the Sichuan Basin of Southwest China: Conversion of cropland to forest ecosystem
260 _ _ |a Amsterdam [u.a.]
|c 2017
|b Elsevier Science
336 7 _ |a article
|2 DRIVER
336 7 _ |a Output Types/Journal article
|2 DataCite
336 7 _ |a Journal Article
|b journal
|m journal
|0 PUB:(DE-HGF)16
|s 1512375171_12600
|2 PUB:(DE-HGF)
336 7 _ |a ARTICLE
|2 BibTeX
336 7 _ |a JOURNAL_ARTICLE
|2 ORCID
336 7 _ |a Journal Article
|0 0
|2 EndNote
520 _ _ |a In the humid subtropics, conversion of cropland to forest has been recognized to influence carbon cycling (e.g., soil CO2 emissions) and the associated ecosystem carbon balance. A three-year field study was conducted in situ to quantitatively evaluate effects of land use change on carbon budget in a cropland (under winter wheat-summer maize rotation) comparison with the adjacent forest ecosystem. During the three-year experimental period, on average, soil heterotrophic respirations were 35.19 mg C·m− 2·h− 1 for the cropland and 40.02 mg C·m− 2·h− 1 for the adjacent forest ecosystem. The quantified net primary production (NPP) were 8724.78 kg C·ha− 1·year− 1 for the cropland (3218.14 kg C·ha− 1 for winter wheat season and 5506.64 kg C·ha− 1 for summer maize season) and 6478.99 kg C·ha− 1·year− 1 for the adjacent forest ecosystem. Thus, the average positive net ecosystem production (NEP) of 5139.33 kg C·ha− 1·year− 1 and 2790.43 kg C·ha− 1·year− 1 were gained in the cropland and the adjacent forest ecosystem, respectively. Nonetheless, if take into consideration of crop grain harvest (i.e., removal), the mean NEP was only 976.69 kg C·ha− 1·year− 1 for cropland which were over three-fold lower than for the adjacent forest ecosystem. The practice of conversion of cropland (maize-wheat rotation system) to forest consequently resulted in an average annual net carbon sequestration of 1813.74 kg C·ha− 1·year− 1 in the study. Therefore, our findings highlight that practices of conversion of subtropical cropland to forest commonly conducted in the last decades act as sinks of atmospheric CO2 in southwest China.
536 _ _ |a 255 - Terrestrial Systems: From Observation to Prediction (POF3-255)
|0 G:(DE-HGF)POF3-255
|c POF3-255
|f POF III
|x 0
588 _ _ |a Dataset connected to CrossRef
700 1 _ |a Zhou, Minghua
|0 P:(DE-Juel1)166012
|b 1
|e Corresponding author
700 1 _ |a Li, Tao
|0 P:(DE-HGF)0
|b 2
700 1 _ |a Ke, Yun
|0 P:(DE-HGF)0
|b 3
700 1 _ |a Zhu, Bo
|0 P:(DE-HGF)0
|b 4
773 _ _ |a 10.1016/j.scitotenv.2017.07.167
|g Vol. 609, p. 556 - 562
|0 PERI:(DE-600)1498726-0
|p 556 - 562
|t The science of the total environment
|v 609
|y 2017
|x 0048-9697
856 4 _ |u https://juser.fz-juelich.de/record/840436/files/1-s2.0-S0048969717318703-main.pdf
|y Restricted
856 4 _ |u https://juser.fz-juelich.de/record/840436/files/1-s2.0-S0048969717318703-main.gif?subformat=icon
|x icon
|y Restricted
856 4 _ |u https://juser.fz-juelich.de/record/840436/files/1-s2.0-S0048969717318703-main.jpg?subformat=icon-1440
|x icon-1440
|y Restricted
856 4 _ |u https://juser.fz-juelich.de/record/840436/files/1-s2.0-S0048969717318703-main.jpg?subformat=icon-180
|x icon-180
|y Restricted
856 4 _ |u https://juser.fz-juelich.de/record/840436/files/1-s2.0-S0048969717318703-main.jpg?subformat=icon-640
|x icon-640
|y Restricted
856 4 _ |u https://juser.fz-juelich.de/record/840436/files/1-s2.0-S0048969717318703-main.pdf?subformat=pdfa
|x pdfa
|y Restricted
909 C O |o oai:juser.fz-juelich.de:840436
|p VDB
|p VDB:Earth_Environment
910 1 _ |a Forschungszentrum Jülich
|0 I:(DE-588b)5008462-8
|k FZJ
|b 1
|6 P:(DE-Juel1)166012
913 1 _ |a DE-HGF
|l Terrestrische Umwelt
|1 G:(DE-HGF)POF3-250
|0 G:(DE-HGF)POF3-255
|2 G:(DE-HGF)POF3-200
|v Terrestrial Systems: From Observation to Prediction
|x 0
|4 G:(DE-HGF)POF
|3 G:(DE-HGF)POF3
|b Erde und Umwelt
914 1 _ |y 2017
915 _ _ |a Nationallizenz
|0 StatID:(DE-HGF)0420
|2 StatID
915 _ _ |a JCR
|0 StatID:(DE-HGF)0100
|2 StatID
|b SCI TOTAL ENVIRON : 2015
915 _ _ |a DBCoverage
|0 StatID:(DE-HGF)0200
|2 StatID
|b SCOPUS
915 _ _ |a DBCoverage
|0 StatID:(DE-HGF)0300
|2 StatID
|b Medline
915 _ _ |a DBCoverage
|0 StatID:(DE-HGF)0310
|2 StatID
|b NCBI Molecular Biology Database
915 _ _ |a DBCoverage
|0 StatID:(DE-HGF)0600
|2 StatID
|b Ebsco Academic Search
915 _ _ |a Peer Review
|0 StatID:(DE-HGF)0030
|2 StatID
|b ASC
915 _ _ |a DBCoverage
|0 StatID:(DE-HGF)0199
|2 StatID
|b Thomson Reuters Master Journal List
915 _ _ |a WoS
|0 StatID:(DE-HGF)0110
|2 StatID
|b Science Citation Index
915 _ _ |a DBCoverage
|0 StatID:(DE-HGF)0150
|2 StatID
|b Web of Science Core Collection
915 _ _ |a WoS
|0 StatID:(DE-HGF)0111
|2 StatID
|b Science Citation Index Expanded
915 _ _ |a DBCoverage
|0 StatID:(DE-HGF)1060
|2 StatID
|b Current Contents - Agriculture, Biology and Environmental Sciences
915 _ _ |a DBCoverage
|0 StatID:(DE-HGF)1050
|2 StatID
|b BIOSIS Previews
915 _ _ |a IF < 5
|0 StatID:(DE-HGF)9900
|2 StatID
920 1 _ |0 I:(DE-Juel1)IBG-3-20101118
|k IBG-3
|l Agrosphäre
|x 0
980 _ _ |a journal
980 _ _ |a VDB
980 _ _ |a I:(DE-Juel1)IBG-3-20101118
980 _ _ |a UNRESTRICTED


LibraryCollectionCLSMajorCLSMinorLanguageAuthor
Marc 21