The bioaccumulation of Cd in rice grains in paddy soils as affected and predicted by soil properties

Purpose The area of cadmium (Cd)-contaminated soil in China is increasing due to the rapid development of the Chinese economy. To ensure that the rice produced in China meets current food safety and quality standards, the current soil quality standards for paddy soils urgently need to be updated. Ma...
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Gespeichert in:

Autor*in:	Ye, Xinxin [verfasserIn] Li, Hongying [verfasserIn] Ma, Yibing [verfasserIn] Wu, Liang [verfasserIn] Sun, Bo [verfasserIn]

Format:	E-Artikel
Sprache:	Englisch

Erschienen:	2014

Schlagwörter:	Bioaccumulation Cd Paddy soil Threshold

Übergeordnetes Werk:	Enthalten in: Journal of soils and sediments - Berlin : Springer, 2001, 14(2014), 8 vom: 25. Apr., Seite 1407-1416
Übergeordnetes Werk:	volume:14 ; year:2014 ; number:8 ; day:25 ; month:04 ; pages:1407-1416

Links:	Volltext

DOI / URN:	10.1007/s11368-014-0901-9

Katalog-ID:	SPR01895622X

Internformat


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245	1	4	\|a The bioaccumulation of Cd in rice grains in paddy soils as affected and predicted by soil properties
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520			\|a Purpose The area of cadmium (Cd)-contaminated soil in China is increasing due to the rapid development of the Chinese economy. To ensure that the rice produced in China meets current food safety and quality standards, the current soil quality standards for paddy soils urgently need to be updated. Materials and methods We conducted a pot experiment with 19 representative paddy soils from different parts of China to study the effects of soil properties on bioaccumulation of Cd in rice grains. The experiment included a control, a low treatment concentration (0.3 mg $ kg^{–1} $ for pH < 6.5 and 0.6 mg $ kg^{–1} $ for pH ≥ 6.5), and a high treatment concentration (0.6 mg $ kg^{–1} $ for pH < 6.5 and 1.2 mg $ kg^{–1} $ for pH ≥ 6.5) of Cd salt added to soils. Results and discussion The results showed that the Cd content in grains of the control and low and high Cd treatments ranged from 0.021 to 0.14, 0.07 to 0.27, and 0.12 to 0.33 mg $ kg^{–1} $, respectively. Stepwise multiple regression analysis indicated that soil pH and organic carbon (OC) content could explain over 60 % of the variance in the (log-transformed) bioaccumulation coefficient (BCF) of Cd in grains across soils. Aggregated boosted trees analysis showed that soil pH and OC were the main factors controlling Cd bioavailability in paddy soils. Validation of the models against data from recent literature indicated that they were able to accurately predict the BCF in paddy soils. Conclusions These quantitative relationships between the BCF of Cd in grains and soil properties are helpful for developing soil-specific guidance on Cd safety threshold value for paddy soils.
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allfields	10.1007/s11368-014-0901-9 doi (DE-627)SPR01895622X (SPR)s11368-014-0901-9-e DE-627 ger DE-627 rakwb eng 550 ASE 58.52 bkl Ye, Xinxin verfasserin aut The bioaccumulation of Cd in rice grains in paddy soils as affected and predicted by soil properties 2014 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Purpose The area of cadmium (Cd)-contaminated soil in China is increasing due to the rapid development of the Chinese economy. To ensure that the rice produced in China meets current food safety and quality standards, the current soil quality standards for paddy soils urgently need to be updated. Materials and methods We conducted a pot experiment with 19 representative paddy soils from different parts of China to study the effects of soil properties on bioaccumulation of Cd in rice grains. The experiment included a control, a low treatment concentration (0.3 mg $ kg^{–1} $ for pH < 6.5 and 0.6 mg $ kg^{–1} $ for pH ≥ 6.5), and a high treatment concentration (0.6 mg $ kg^{–1} $ for pH < 6.5 and 1.2 mg $ kg^{–1} $ for pH ≥ 6.5) of Cd salt added to soils. Results and discussion The results showed that the Cd content in grains of the control and low and high Cd treatments ranged from 0.021 to 0.14, 0.07 to 0.27, and 0.12 to 0.33 mg $ kg^{–1} $, respectively. Stepwise multiple regression analysis indicated that soil pH and organic carbon (OC) content could explain over 60 % of the variance in the (log-transformed) bioaccumulation coefficient (BCF) of Cd in grains across soils. Aggregated boosted trees analysis showed that soil pH and OC were the main factors controlling Cd bioavailability in paddy soils. Validation of the models against data from recent literature indicated that they were able to accurately predict the BCF in paddy soils. Conclusions These quantitative relationships between the BCF of Cd in grains and soil properties are helpful for developing soil-specific guidance on Cd safety threshold value for paddy soils. Bioaccumulation (dpeaa)DE-He213 Cd (dpeaa)DE-He213 Paddy soil (dpeaa)DE-He213 Threshold (dpeaa)DE-He213 Li, Hongying verfasserin aut Ma, Yibing verfasserin aut Wu, Liang verfasserin aut Sun, Bo verfasserin aut Enthalten in Journal of soils and sediments Berlin : Springer, 2001 14(2014), 8 vom: 25. Apr., Seite 1407-1416 (DE-627)373325134 (DE-600)2125896-X 1614-7480 nnns volume:14 year:2014 number:8 day:25 month:04 pages:1407-1416 https://dx.doi.org/10.1007/s11368-014-0901-9 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_183 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 58.52 ASE AR 14 2014 8 25 04 1407-1416
spelling	10.1007/s11368-014-0901-9 doi (DE-627)SPR01895622X (SPR)s11368-014-0901-9-e DE-627 ger DE-627 rakwb eng 550 ASE 58.52 bkl Ye, Xinxin verfasserin aut The bioaccumulation of Cd in rice grains in paddy soils as affected and predicted by soil properties 2014 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Purpose The area of cadmium (Cd)-contaminated soil in China is increasing due to the rapid development of the Chinese economy. To ensure that the rice produced in China meets current food safety and quality standards, the current soil quality standards for paddy soils urgently need to be updated. Materials and methods We conducted a pot experiment with 19 representative paddy soils from different parts of China to study the effects of soil properties on bioaccumulation of Cd in rice grains. The experiment included a control, a low treatment concentration (0.3 mg $ kg^{–1} $ for pH < 6.5 and 0.6 mg $ kg^{–1} $ for pH ≥ 6.5), and a high treatment concentration (0.6 mg $ kg^{–1} $ for pH < 6.5 and 1.2 mg $ kg^{–1} $ for pH ≥ 6.5) of Cd salt added to soils. Results and discussion The results showed that the Cd content in grains of the control and low and high Cd treatments ranged from 0.021 to 0.14, 0.07 to 0.27, and 0.12 to 0.33 mg $ kg^{–1} $, respectively. Stepwise multiple regression analysis indicated that soil pH and organic carbon (OC) content could explain over 60 % of the variance in the (log-transformed) bioaccumulation coefficient (BCF) of Cd in grains across soils. Aggregated boosted trees analysis showed that soil pH and OC were the main factors controlling Cd bioavailability in paddy soils. Validation of the models against data from recent literature indicated that they were able to accurately predict the BCF in paddy soils. Conclusions These quantitative relationships between the BCF of Cd in grains and soil properties are helpful for developing soil-specific guidance on Cd safety threshold value for paddy soils. Bioaccumulation (dpeaa)DE-He213 Cd (dpeaa)DE-He213 Paddy soil (dpeaa)DE-He213 Threshold (dpeaa)DE-He213 Li, Hongying verfasserin aut Ma, Yibing verfasserin aut Wu, Liang verfasserin aut Sun, Bo verfasserin aut Enthalten in Journal of soils and sediments Berlin : Springer, 2001 14(2014), 8 vom: 25. Apr., Seite 1407-1416 (DE-627)373325134 (DE-600)2125896-X 1614-7480 nnns volume:14 year:2014 number:8 day:25 month:04 pages:1407-1416 https://dx.doi.org/10.1007/s11368-014-0901-9 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_183 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 58.52 ASE AR 14 2014 8 25 04 1407-1416
allfields_unstemmed	10.1007/s11368-014-0901-9 doi (DE-627)SPR01895622X (SPR)s11368-014-0901-9-e DE-627 ger DE-627 rakwb eng 550 ASE 58.52 bkl Ye, Xinxin verfasserin aut The bioaccumulation of Cd in rice grains in paddy soils as affected and predicted by soil properties 2014 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Purpose The area of cadmium (Cd)-contaminated soil in China is increasing due to the rapid development of the Chinese economy. To ensure that the rice produced in China meets current food safety and quality standards, the current soil quality standards for paddy soils urgently need to be updated. Materials and methods We conducted a pot experiment with 19 representative paddy soils from different parts of China to study the effects of soil properties on bioaccumulation of Cd in rice grains. The experiment included a control, a low treatment concentration (0.3 mg $ kg^{–1} $ for pH < 6.5 and 0.6 mg $ kg^{–1} $ for pH ≥ 6.5), and a high treatment concentration (0.6 mg $ kg^{–1} $ for pH < 6.5 and 1.2 mg $ kg^{–1} $ for pH ≥ 6.5) of Cd salt added to soils. Results and discussion The results showed that the Cd content in grains of the control and low and high Cd treatments ranged from 0.021 to 0.14, 0.07 to 0.27, and 0.12 to 0.33 mg $ kg^{–1} $, respectively. Stepwise multiple regression analysis indicated that soil pH and organic carbon (OC) content could explain over 60 % of the variance in the (log-transformed) bioaccumulation coefficient (BCF) of Cd in grains across soils. Aggregated boosted trees analysis showed that soil pH and OC were the main factors controlling Cd bioavailability in paddy soils. Validation of the models against data from recent literature indicated that they were able to accurately predict the BCF in paddy soils. Conclusions These quantitative relationships between the BCF of Cd in grains and soil properties are helpful for developing soil-specific guidance on Cd safety threshold value for paddy soils. Bioaccumulation (dpeaa)DE-He213 Cd (dpeaa)DE-He213 Paddy soil (dpeaa)DE-He213 Threshold (dpeaa)DE-He213 Li, Hongying verfasserin aut Ma, Yibing verfasserin aut Wu, Liang verfasserin aut Sun, Bo verfasserin aut Enthalten in Journal of soils and sediments Berlin : Springer, 2001 14(2014), 8 vom: 25. Apr., Seite 1407-1416 (DE-627)373325134 (DE-600)2125896-X 1614-7480 nnns volume:14 year:2014 number:8 day:25 month:04 pages:1407-1416 https://dx.doi.org/10.1007/s11368-014-0901-9 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_183 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 58.52 ASE AR 14 2014 8 25 04 1407-1416
allfieldsGer	10.1007/s11368-014-0901-9 doi (DE-627)SPR01895622X (SPR)s11368-014-0901-9-e DE-627 ger DE-627 rakwb eng 550 ASE 58.52 bkl Ye, Xinxin verfasserin aut The bioaccumulation of Cd in rice grains in paddy soils as affected and predicted by soil properties 2014 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Purpose The area of cadmium (Cd)-contaminated soil in China is increasing due to the rapid development of the Chinese economy. To ensure that the rice produced in China meets current food safety and quality standards, the current soil quality standards for paddy soils urgently need to be updated. Materials and methods We conducted a pot experiment with 19 representative paddy soils from different parts of China to study the effects of soil properties on bioaccumulation of Cd in rice grains. The experiment included a control, a low treatment concentration (0.3 mg $ kg^{–1} $ for pH < 6.5 and 0.6 mg $ kg^{–1} $ for pH ≥ 6.5), and a high treatment concentration (0.6 mg $ kg^{–1} $ for pH < 6.5 and 1.2 mg $ kg^{–1} $ for pH ≥ 6.5) of Cd salt added to soils. Results and discussion The results showed that the Cd content in grains of the control and low and high Cd treatments ranged from 0.021 to 0.14, 0.07 to 0.27, and 0.12 to 0.33 mg $ kg^{–1} $, respectively. Stepwise multiple regression analysis indicated that soil pH and organic carbon (OC) content could explain over 60 % of the variance in the (log-transformed) bioaccumulation coefficient (BCF) of Cd in grains across soils. Aggregated boosted trees analysis showed that soil pH and OC were the main factors controlling Cd bioavailability in paddy soils. Validation of the models against data from recent literature indicated that they were able to accurately predict the BCF in paddy soils. Conclusions These quantitative relationships between the BCF of Cd in grains and soil properties are helpful for developing soil-specific guidance on Cd safety threshold value for paddy soils. Bioaccumulation (dpeaa)DE-He213 Cd (dpeaa)DE-He213 Paddy soil (dpeaa)DE-He213 Threshold (dpeaa)DE-He213 Li, Hongying verfasserin aut Ma, Yibing verfasserin aut Wu, Liang verfasserin aut Sun, Bo verfasserin aut Enthalten in Journal of soils and sediments Berlin : Springer, 2001 14(2014), 8 vom: 25. Apr., Seite 1407-1416 (DE-627)373325134 (DE-600)2125896-X 1614-7480 nnns volume:14 year:2014 number:8 day:25 month:04 pages:1407-1416 https://dx.doi.org/10.1007/s11368-014-0901-9 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_183 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 58.52 ASE AR 14 2014 8 25 04 1407-1416
allfieldsSound	10.1007/s11368-014-0901-9 doi (DE-627)SPR01895622X (SPR)s11368-014-0901-9-e DE-627 ger DE-627 rakwb eng 550 ASE 58.52 bkl Ye, Xinxin verfasserin aut The bioaccumulation of Cd in rice grains in paddy soils as affected and predicted by soil properties 2014 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Purpose The area of cadmium (Cd)-contaminated soil in China is increasing due to the rapid development of the Chinese economy. To ensure that the rice produced in China meets current food safety and quality standards, the current soil quality standards for paddy soils urgently need to be updated. Materials and methods We conducted a pot experiment with 19 representative paddy soils from different parts of China to study the effects of soil properties on bioaccumulation of Cd in rice grains. The experiment included a control, a low treatment concentration (0.3 mg $ kg^{–1} $ for pH < 6.5 and 0.6 mg $ kg^{–1} $ for pH ≥ 6.5), and a high treatment concentration (0.6 mg $ kg^{–1} $ for pH < 6.5 and 1.2 mg $ kg^{–1} $ for pH ≥ 6.5) of Cd salt added to soils. Results and discussion The results showed that the Cd content in grains of the control and low and high Cd treatments ranged from 0.021 to 0.14, 0.07 to 0.27, and 0.12 to 0.33 mg $ kg^{–1} $, respectively. Stepwise multiple regression analysis indicated that soil pH and organic carbon (OC) content could explain over 60 % of the variance in the (log-transformed) bioaccumulation coefficient (BCF) of Cd in grains across soils. Aggregated boosted trees analysis showed that soil pH and OC were the main factors controlling Cd bioavailability in paddy soils. Validation of the models against data from recent literature indicated that they were able to accurately predict the BCF in paddy soils. Conclusions These quantitative relationships between the BCF of Cd in grains and soil properties are helpful for developing soil-specific guidance on Cd safety threshold value for paddy soils. Bioaccumulation (dpeaa)DE-He213 Cd (dpeaa)DE-He213 Paddy soil (dpeaa)DE-He213 Threshold (dpeaa)DE-He213 Li, Hongying verfasserin aut Ma, Yibing verfasserin aut Wu, Liang verfasserin aut Sun, Bo verfasserin aut Enthalten in Journal of soils and sediments Berlin : Springer, 2001 14(2014), 8 vom: 25. Apr., Seite 1407-1416 (DE-627)373325134 (DE-600)2125896-X 1614-7480 nnns volume:14 year:2014 number:8 day:25 month:04 pages:1407-1416 https://dx.doi.org/10.1007/s11368-014-0901-9 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_183 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 58.52 ASE AR 14 2014 8 25 04 1407-1416
language	English
source	Enthalten in Journal of soils and sediments 14(2014), 8 vom: 25. Apr., Seite 1407-1416 volume:14 year:2014 number:8 day:25 month:04 pages:1407-1416
sourceStr	Enthalten in Journal of soils and sediments 14(2014), 8 vom: 25. Apr., Seite 1407-1416 volume:14 year:2014 number:8 day:25 month:04 pages:1407-1416
format_phy_str_mv	Article
institution	findex.gbv.de
topic_facet	Bioaccumulation Cd Paddy soil Threshold
dewey-raw	550
isfreeaccess_bool	false
container_title	Journal of soils and sediments
authorswithroles_txt_mv	Ye, Xinxin @@aut@@ Li, Hongying @@aut@@ Ma, Yibing @@aut@@ Wu, Liang @@aut@@ Sun, Bo @@aut@@
publishDateDaySort_date	2014-04-25T00:00:00Z
hierarchy_top_id	373325134
dewey-sort	3550
id	SPR01895622X
language_de	englisch
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To ensure that the rice produced in China meets current food safety and quality standards, the current soil quality standards for paddy soils urgently need to be updated. Materials and methods We conducted a pot experiment with 19 representative paddy soils from different parts of China to study the effects of soil properties on bioaccumulation of Cd in rice grains. The experiment included a control, a low treatment concentration (0.3 mg $ kg^{–1} $ for pH < 6.5 and 0.6 mg $ kg^{–1} $ for pH ≥ 6.5), and a high treatment concentration (0.6 mg $ kg^{–1} $ for pH < 6.5 and 1.2 mg $ kg^{–1} $ for pH ≥ 6.5) of Cd salt added to soils. Results and discussion The results showed that the Cd content in grains of the control and low and high Cd treatments ranged from 0.021 to 0.14, 0.07 to 0.27, and 0.12 to 0.33 mg $ kg^{–1} $, respectively. Stepwise multiple regression analysis indicated that soil pH and organic carbon (OC) content could explain over 60 % of the variance in the (log-transformed) bioaccumulation coefficient (BCF) of Cd in grains across soils. Aggregated boosted trees analysis showed that soil pH and OC were the main factors controlling Cd bioavailability in paddy soils. Validation of the models against data from recent literature indicated that they were able to accurately predict the BCF in paddy soils. 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author	Ye, Xinxin
spellingShingle	Ye, Xinxin ddc 550 bkl 58.52 misc Bioaccumulation misc Cd misc Paddy soil misc Threshold The bioaccumulation of Cd in rice grains in paddy soils as affected and predicted by soil properties
authorStr	Ye, Xinxin
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topic_title	550 ASE 58.52 bkl The bioaccumulation of Cd in rice grains in paddy soils as affected and predicted by soil properties Bioaccumulation (dpeaa)DE-He213 Cd (dpeaa)DE-He213 Paddy soil (dpeaa)DE-He213 Threshold (dpeaa)DE-He213
topic	ddc 550 bkl 58.52 misc Bioaccumulation misc Cd misc Paddy soil misc Threshold
topic_unstemmed	ddc 550 bkl 58.52 misc Bioaccumulation misc Cd misc Paddy soil misc Threshold
topic_browse	ddc 550 bkl 58.52 misc Bioaccumulation misc Cd misc Paddy soil misc Threshold
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hierarchy_parent_title	Journal of soils and sediments
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title	The bioaccumulation of Cd in rice grains in paddy soils as affected and predicted by soil properties
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title_full	The bioaccumulation of Cd in rice grains in paddy soils as affected and predicted by soil properties
author_sort	Ye, Xinxin
journal	Journal of soils and sediments
journalStr	Journal of soils and sediments
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author_browse	Ye, Xinxin Li, Hongying Ma, Yibing Wu, Liang Sun, Bo
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doi_str_mv	10.1007/s11368-014-0901-9
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title_sort	bioaccumulation of cd in rice grains in paddy soils as affected and predicted by soil properties
title_auth	The bioaccumulation of Cd in rice grains in paddy soils as affected and predicted by soil properties
abstract	Purpose The area of cadmium (Cd)-contaminated soil in China is increasing due to the rapid development of the Chinese economy. To ensure that the rice produced in China meets current food safety and quality standards, the current soil quality standards for paddy soils urgently need to be updated. Materials and methods We conducted a pot experiment with 19 representative paddy soils from different parts of China to study the effects of soil properties on bioaccumulation of Cd in rice grains. The experiment included a control, a low treatment concentration (0.3 mg $ kg^{–1} $ for pH < 6.5 and 0.6 mg $ kg^{–1} $ for pH ≥ 6.5), and a high treatment concentration (0.6 mg $ kg^{–1} $ for pH < 6.5 and 1.2 mg $ kg^{–1} $ for pH ≥ 6.5) of Cd salt added to soils. Results and discussion The results showed that the Cd content in grains of the control and low and high Cd treatments ranged from 0.021 to 0.14, 0.07 to 0.27, and 0.12 to 0.33 mg $ kg^{–1} $, respectively. Stepwise multiple regression analysis indicated that soil pH and organic carbon (OC) content could explain over 60 % of the variance in the (log-transformed) bioaccumulation coefficient (BCF) of Cd in grains across soils. Aggregated boosted trees analysis showed that soil pH and OC were the main factors controlling Cd bioavailability in paddy soils. Validation of the models against data from recent literature indicated that they were able to accurately predict the BCF in paddy soils. Conclusions These quantitative relationships between the BCF of Cd in grains and soil properties are helpful for developing soil-specific guidance on Cd safety threshold value for paddy soils.
abstractGer	Purpose The area of cadmium (Cd)-contaminated soil in China is increasing due to the rapid development of the Chinese economy. To ensure that the rice produced in China meets current food safety and quality standards, the current soil quality standards for paddy soils urgently need to be updated. Materials and methods We conducted a pot experiment with 19 representative paddy soils from different parts of China to study the effects of soil properties on bioaccumulation of Cd in rice grains. The experiment included a control, a low treatment concentration (0.3 mg $ kg^{–1} $ for pH < 6.5 and 0.6 mg $ kg^{–1} $ for pH ≥ 6.5), and a high treatment concentration (0.6 mg $ kg^{–1} $ for pH < 6.5 and 1.2 mg $ kg^{–1} $ for pH ≥ 6.5) of Cd salt added to soils. Results and discussion The results showed that the Cd content in grains of the control and low and high Cd treatments ranged from 0.021 to 0.14, 0.07 to 0.27, and 0.12 to 0.33 mg $ kg^{–1} $, respectively. Stepwise multiple regression analysis indicated that soil pH and organic carbon (OC) content could explain over 60 % of the variance in the (log-transformed) bioaccumulation coefficient (BCF) of Cd in grains across soils. Aggregated boosted trees analysis showed that soil pH and OC were the main factors controlling Cd bioavailability in paddy soils. Validation of the models against data from recent literature indicated that they were able to accurately predict the BCF in paddy soils. Conclusions These quantitative relationships between the BCF of Cd in grains and soil properties are helpful for developing soil-specific guidance on Cd safety threshold value for paddy soils.
abstract_unstemmed	Purpose The area of cadmium (Cd)-contaminated soil in China is increasing due to the rapid development of the Chinese economy. To ensure that the rice produced in China meets current food safety and quality standards, the current soil quality standards for paddy soils urgently need to be updated. Materials and methods We conducted a pot experiment with 19 representative paddy soils from different parts of China to study the effects of soil properties on bioaccumulation of Cd in rice grains. The experiment included a control, a low treatment concentration (0.3 mg $ kg^{–1} $ for pH < 6.5 and 0.6 mg $ kg^{–1} $ for pH ≥ 6.5), and a high treatment concentration (0.6 mg $ kg^{–1} $ for pH < 6.5 and 1.2 mg $ kg^{–1} $ for pH ≥ 6.5) of Cd salt added to soils. Results and discussion The results showed that the Cd content in grains of the control and low and high Cd treatments ranged from 0.021 to 0.14, 0.07 to 0.27, and 0.12 to 0.33 mg $ kg^{–1} $, respectively. Stepwise multiple regression analysis indicated that soil pH and organic carbon (OC) content could explain over 60 % of the variance in the (log-transformed) bioaccumulation coefficient (BCF) of Cd in grains across soils. Aggregated boosted trees analysis showed that soil pH and OC were the main factors controlling Cd bioavailability in paddy soils. Validation of the models against data from recent literature indicated that they were able to accurately predict the BCF in paddy soils. Conclusions These quantitative relationships between the BCF of Cd in grains and soil properties are helpful for developing soil-specific guidance on Cd safety threshold value for paddy soils.
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container_issue	8
title_short	The bioaccumulation of Cd in rice grains in paddy soils as affected and predicted by soil properties
url	https://dx.doi.org/10.1007/s11368-014-0901-9
remote_bool	true
author2	Li, Hongying Ma, Yibing Wu, Liang Sun, Bo
author2Str	Li, Hongying Ma, Yibing Wu, Liang Sun, Bo
ppnlink	373325134
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doi_str	10.1007/s11368-014-0901-9
up_date	2024-07-03T23:24:52.731Z
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To ensure that the rice produced in China meets current food safety and quality standards, the current soil quality standards for paddy soils urgently need to be updated. Materials and methods We conducted a pot experiment with 19 representative paddy soils from different parts of China to study the effects of soil properties on bioaccumulation of Cd in rice grains. The experiment included a control, a low treatment concentration (0.3 mg $ kg^{–1} $ for pH < 6.5 and 0.6 mg $ kg^{–1} $ for pH ≥ 6.5), and a high treatment concentration (0.6 mg $ kg^{–1} $ for pH < 6.5 and 1.2 mg $ kg^{–1} $ for pH ≥ 6.5) of Cd salt added to soils. Results and discussion The results showed that the Cd content in grains of the control and low and high Cd treatments ranged from 0.021 to 0.14, 0.07 to 0.27, and 0.12 to 0.33 mg $ kg^{–1} $, respectively. Stepwise multiple regression analysis indicated that soil pH and organic carbon (OC) content could explain over 60 % of the variance in the (log-transformed) bioaccumulation coefficient (BCF) of Cd in grains across soils. Aggregated boosted trees analysis showed that soil pH and OC were the main factors controlling Cd bioavailability in paddy soils. Validation of the models against data from recent literature indicated that they were able to accurately predict the BCF in paddy soils. 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The bioaccumulation of Cd in rice grains in paddy soils as affected and predicted by soil properties

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