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Effect of vegetation on soil C, N, P and other minerals in Oxisols at the forest-savanna transition zone of central Africa
The forest-savanna transition zone, which evolves as a result of past climate change, is widely distributed in central Africa. Because nutrient-poor soils (Oxisols) are widely distributed in this area, it is necessary to understand the characteristics of soil nutrients in relation to the vegetation....
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Published in: | Soil science and plant nutrition (Tokyo) 2014-01, Vol.60 (1), p.45-59 |
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description | The forest-savanna transition zone, which evolves as a result of past climate change, is widely distributed in central Africa. Because nutrient-poor soils (Oxisols) are widely distributed in this area, it is necessary to understand the characteristics of soil nutrients in relation to the vegetation. We collected 52 soil samples from five pits each for two different vegetation types (forest and savanna) in this area and evaluated the effect of vegetation type on soil physicochemical properties [pH, soil texture, cation-exchange capacity, bulk density, crystalline and non-crystalline aluminum (Al) and iron (Fe)] and nutrient status [carbon (C), nitrogen (N), phosphorus (P) and other soil minerals]. We also evaluated the fractionated P. Whereas most physicochemical properties were similar between the two vegetation types throughout the soil profile (0–80 cm depth), clay content, bulk density and soil pH clearly differed between the vegetations at the surface layer (0–10 cm). At 80 cm soil depth, soil C, N and P were 87.9, 7.7 and 3.7 Mg ha ⁻¹, respectively, in forest, and 98.6, 7.1 and 3.1 Mg ha ⁻¹, respectively, in savanna. Although there was no clear difference between the amounts of soil C, N and P, the upper-soil (0–40 cm) C:N ratio was clearly lower in forest (11.0–12.0) compared with savanna (13.0–15.7), because the main plant species in the forest can fix N effectively. We also found a smaller ratio of sodium hydroxide (NaOH)-extractable inorganic P to total soil P in forest compared with savanna. Because the content of crystalline and non-crystalline Al and Fe in forest soil was similar to that of savanna, the different soil C:N ratio would cause different availability of P between the vegetation types, although the mechanism is unclear. These results indicate that savanna vegetation is N-limited and forest vegetation is N-saturated (and possibly P-limited) in this zone. We also found that, at 20 cm soil depth, total soil potassium (K) in forest was 1590 kg ha ⁻¹, which was 930 kg ha ⁻¹ less than that in savanna (2520 kg ha ⁻¹; P |
doi_str_mv | 10.1080/00380768.2013.866523 |
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Because nutrient-poor soils (Oxisols) are widely distributed in this area, it is necessary to understand the characteristics of soil nutrients in relation to the vegetation. We collected 52 soil samples from five pits each for two different vegetation types (forest and savanna) in this area and evaluated the effect of vegetation type on soil physicochemical properties [pH, soil texture, cation-exchange capacity, bulk density, crystalline and non-crystalline aluminum (Al) and iron (Fe)] and nutrient status [carbon (C), nitrogen (N), phosphorus (P) and other soil minerals]. We also evaluated the fractionated P. Whereas most physicochemical properties were similar between the two vegetation types throughout the soil profile (0–80 cm depth), clay content, bulk density and soil pH clearly differed between the vegetations at the surface layer (0–10 cm). At 80 cm soil depth, soil C, N and P were 87.9, 7.7 and 3.7 Mg ha ⁻¹, respectively, in forest, and 98.6, 7.1 and 3.1 Mg ha ⁻¹, respectively, in savanna. Although there was no clear difference between the amounts of soil C, N and P, the upper-soil (0–40 cm) C:N ratio was clearly lower in forest (11.0–12.0) compared with savanna (13.0–15.7), because the main plant species in the forest can fix N effectively. We also found a smaller ratio of sodium hydroxide (NaOH)-extractable inorganic P to total soil P in forest compared with savanna. Because the content of crystalline and non-crystalline Al and Fe in forest soil was similar to that of savanna, the different soil C:N ratio would cause different availability of P between the vegetation types, although the mechanism is unclear. These results indicate that savanna vegetation is N-limited and forest vegetation is N-saturated (and possibly P-limited) in this zone. We also found that, at 20 cm soil depth, total soil potassium (K) in forest was 1590 kg ha ⁻¹, which was 930 kg ha ⁻¹ less than that in savanna (2520 kg ha ⁻¹; P < 0.05), although a similar difference was not measured for Na, Ca, and magnesium (Mg). Because we observed lower soil pH in forest, not only plant K uptake but also K leaching loss would contribute to lower soil K in forest.</description><identifier>ISSN: 1747-0765</identifier><identifier>ISSN: 0038-0768</identifier><identifier>EISSN: 1747-0765</identifier><identifier>DOI: 10.1080/00380768.2013.866523</identifier><language>eng</language><publisher>Kyoto: Taylor & Francis</publisher><subject>aluminum ; bulk density ; calcium ; carbon ; carbon nitrogen ratio ; cation exchange capacity ; clay fraction ; climate change ; forest soils ; Forest-savanna transition zone ; forests ; fractionated phosphorus ; iron ; leaching ; magnesium ; minerals ; nitrogen ; Oxisols ; phosphorus ; potassium ; savannas ; sodium ; sodium hydroxide ; soil C:N ratio ; soil density ; soil depth ; soil minerals ; soil nutrients ; soil pH ; soil profiles ; soil sampling ; soil texture</subject><ispartof>Soil science and plant nutrition (Tokyo), 2014-01, Vol.60 (1), p.45-59</ispartof><rights>2014 Japanese Society of Soil Science and Plant Nutrition 2014</rights><rights>2014 Japanese Society of Soil Science and Plant Nutrition</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c458t-c595a61e8a2b3f63e5f631a2b2f17e01ba1f093791c0e835fdbece76c1fea6863</citedby><cites>FETCH-LOGICAL-c458t-c595a61e8a2b3f63e5f631a2b2f17e01ba1f093791c0e835fdbece76c1fea6863</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,780,784,27924,27925</link.rule.ids></links><search><creatorcontrib>Sugihara, Soh</creatorcontrib><creatorcontrib>Shibata, Makoto</creatorcontrib><creatorcontrib>Mvondo Ze, Antonie D</creatorcontrib><creatorcontrib>Araki, Shigeru</creatorcontrib><creatorcontrib>Funakawa, Shinya</creatorcontrib><title>Effect of vegetation on soil C, N, P and other minerals in Oxisols at the forest-savanna transition zone of central Africa</title><title>Soil science and plant nutrition (Tokyo)</title><description>The forest-savanna transition zone, which evolves as a result of past climate change, is widely distributed in central Africa. Because nutrient-poor soils (Oxisols) are widely distributed in this area, it is necessary to understand the characteristics of soil nutrients in relation to the vegetation. We collected 52 soil samples from five pits each for two different vegetation types (forest and savanna) in this area and evaluated the effect of vegetation type on soil physicochemical properties [pH, soil texture, cation-exchange capacity, bulk density, crystalline and non-crystalline aluminum (Al) and iron (Fe)] and nutrient status [carbon (C), nitrogen (N), phosphorus (P) and other soil minerals]. We also evaluated the fractionated P. Whereas most physicochemical properties were similar between the two vegetation types throughout the soil profile (0–80 cm depth), clay content, bulk density and soil pH clearly differed between the vegetations at the surface layer (0–10 cm). At 80 cm soil depth, soil C, N and P were 87.9, 7.7 and 3.7 Mg ha ⁻¹, respectively, in forest, and 98.6, 7.1 and 3.1 Mg ha ⁻¹, respectively, in savanna. Although there was no clear difference between the amounts of soil C, N and P, the upper-soil (0–40 cm) C:N ratio was clearly lower in forest (11.0–12.0) compared with savanna (13.0–15.7), because the main plant species in the forest can fix N effectively. We also found a smaller ratio of sodium hydroxide (NaOH)-extractable inorganic P to total soil P in forest compared with savanna. Because the content of crystalline and non-crystalline Al and Fe in forest soil was similar to that of savanna, the different soil C:N ratio would cause different availability of P between the vegetation types, although the mechanism is unclear. These results indicate that savanna vegetation is N-limited and forest vegetation is N-saturated (and possibly P-limited) in this zone. We also found that, at 20 cm soil depth, total soil potassium (K) in forest was 1590 kg ha ⁻¹, which was 930 kg ha ⁻¹ less than that in savanna (2520 kg ha ⁻¹; P < 0.05), although a similar difference was not measured for Na, Ca, and magnesium (Mg). Because we observed lower soil pH in forest, not only plant K uptake but also K leaching loss would contribute to lower soil K in forest.</description><subject>aluminum</subject><subject>bulk density</subject><subject>calcium</subject><subject>carbon</subject><subject>carbon nitrogen ratio</subject><subject>cation exchange capacity</subject><subject>clay fraction</subject><subject>climate change</subject><subject>forest soils</subject><subject>Forest-savanna transition zone</subject><subject>forests</subject><subject>fractionated phosphorus</subject><subject>iron</subject><subject>leaching</subject><subject>magnesium</subject><subject>minerals</subject><subject>nitrogen</subject><subject>Oxisols</subject><subject>phosphorus</subject><subject>potassium</subject><subject>savannas</subject><subject>sodium</subject><subject>sodium hydroxide</subject><subject>soil C:N ratio</subject><subject>soil density</subject><subject>soil depth</subject><subject>soil minerals</subject><subject>soil nutrients</subject><subject>soil pH</subject><subject>soil profiles</subject><subject>soil sampling</subject><subject>soil texture</subject><issn>1747-0765</issn><issn>0038-0768</issn><issn>1747-0765</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2014</creationdate><recordtype>article</recordtype><recordid>eNqFUV1LHTEQXUoLtdp_UGigL31wr8lmk80-FbnYDxAVrM9hbu7ERvYmNsnV6q_vXLdC6UshJDOTc84Mc5rmneALwQ0_4lwaPmiz6LiQC6O16uSLZk8M_dBSXb38K37dvCnlhvO-l6rbax5PvEdXWfLsDq-xQg0pMjolhYktD9nZIbtgENcs1R-Y2SZEzDAVFiI7_xVKohAqoz_mU8ZS2wJ3ECOwmiGW8CT3mCLuOjiMVJ3Ysc_BwUHzypMSvv3z7jdXn0--L7-2p-dfvi2PT1vXK1Nbp0YFWqCBbiW9lqjoEpR0XgzIxQqE56McRuE4Gqn8eoUOB-2ER9BGy_3m46x7m9PPLY1oN6E4nCaImLbFCiV7IwYxdgT98A_0Jm1zpOkI1SnqoZ5Q_YxyOZWS0dvbHDaQH6zgdmeIfTbE7gyxsyFE-zTTQqRVbeA-5WltKzxMKXtalgvFyv8ovJ8VPCQL15kIV5cEUJwLo8Uwyt9WpJqr</recordid><startdate>20140102</startdate><enddate>20140102</enddate><creator>Sugihara, Soh</creator><creator>Shibata, Makoto</creator><creator>Mvondo Ze, Antonie D</creator><creator>Araki, Shigeru</creator><creator>Funakawa, Shinya</creator><general>Taylor & Francis</general><general>Taylor & Francis Ltd</general><scope>FBQ</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7QL</scope><scope>7T7</scope><scope>7U9</scope><scope>8FD</scope><scope>C1K</scope><scope>FR3</scope><scope>H94</scope><scope>M7N</scope><scope>P64</scope><scope>7QH</scope><scope>7UA</scope></search><sort><creationdate>20140102</creationdate><title>Effect of vegetation on soil C, N, P and other minerals in Oxisols at the forest-savanna transition zone of central Africa</title><author>Sugihara, Soh ; Shibata, Makoto ; Mvondo Ze, Antonie D ; Araki, Shigeru ; Funakawa, Shinya</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c458t-c595a61e8a2b3f63e5f631a2b2f17e01ba1f093791c0e835fdbece76c1fea6863</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2014</creationdate><topic>aluminum</topic><topic>bulk density</topic><topic>calcium</topic><topic>carbon</topic><topic>carbon nitrogen ratio</topic><topic>cation exchange capacity</topic><topic>clay fraction</topic><topic>climate change</topic><topic>forest soils</topic><topic>Forest-savanna transition zone</topic><topic>forests</topic><topic>fractionated phosphorus</topic><topic>iron</topic><topic>leaching</topic><topic>magnesium</topic><topic>minerals</topic><topic>nitrogen</topic><topic>Oxisols</topic><topic>phosphorus</topic><topic>potassium</topic><topic>savannas</topic><topic>sodium</topic><topic>sodium hydroxide</topic><topic>soil C:N ratio</topic><topic>soil density</topic><topic>soil depth</topic><topic>soil minerals</topic><topic>soil nutrients</topic><topic>soil pH</topic><topic>soil profiles</topic><topic>soil sampling</topic><topic>soil texture</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Sugihara, Soh</creatorcontrib><creatorcontrib>Shibata, Makoto</creatorcontrib><creatorcontrib>Mvondo Ze, Antonie D</creatorcontrib><creatorcontrib>Araki, Shigeru</creatorcontrib><creatorcontrib>Funakawa, Shinya</creatorcontrib><collection>AGRIS</collection><collection>CrossRef</collection><collection>Bacteriology Abstracts (Microbiology B)</collection><collection>Industrial and Applied Microbiology Abstracts (Microbiology A)</collection><collection>Virology and AIDS Abstracts</collection><collection>Technology Research Database</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Engineering Research Database</collection><collection>AIDS and Cancer Research Abstracts</collection><collection>Algology Mycology and Protozoology Abstracts (Microbiology C)</collection><collection>Biotechnology and BioEngineering Abstracts</collection><collection>Aqualine</collection><collection>Water Resources Abstracts</collection><jtitle>Soil science and plant nutrition (Tokyo)</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Sugihara, Soh</au><au>Shibata, Makoto</au><au>Mvondo Ze, Antonie D</au><au>Araki, Shigeru</au><au>Funakawa, Shinya</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Effect of vegetation on soil C, N, P and other minerals in Oxisols at the forest-savanna transition zone of central Africa</atitle><jtitle>Soil science and plant nutrition (Tokyo)</jtitle><date>2014-01-02</date><risdate>2014</risdate><volume>60</volume><issue>1</issue><spage>45</spage><epage>59</epage><pages>45-59</pages><issn>1747-0765</issn><issn>0038-0768</issn><eissn>1747-0765</eissn><abstract>The forest-savanna transition zone, which evolves as a result of past climate change, is widely distributed in central Africa. Because nutrient-poor soils (Oxisols) are widely distributed in this area, it is necessary to understand the characteristics of soil nutrients in relation to the vegetation. We collected 52 soil samples from five pits each for two different vegetation types (forest and savanna) in this area and evaluated the effect of vegetation type on soil physicochemical properties [pH, soil texture, cation-exchange capacity, bulk density, crystalline and non-crystalline aluminum (Al) and iron (Fe)] and nutrient status [carbon (C), nitrogen (N), phosphorus (P) and other soil minerals]. We also evaluated the fractionated P. Whereas most physicochemical properties were similar between the two vegetation types throughout the soil profile (0–80 cm depth), clay content, bulk density and soil pH clearly differed between the vegetations at the surface layer (0–10 cm). At 80 cm soil depth, soil C, N and P were 87.9, 7.7 and 3.7 Mg ha ⁻¹, respectively, in forest, and 98.6, 7.1 and 3.1 Mg ha ⁻¹, respectively, in savanna. Although there was no clear difference between the amounts of soil C, N and P, the upper-soil (0–40 cm) C:N ratio was clearly lower in forest (11.0–12.0) compared with savanna (13.0–15.7), because the main plant species in the forest can fix N effectively. We also found a smaller ratio of sodium hydroxide (NaOH)-extractable inorganic P to total soil P in forest compared with savanna. Because the content of crystalline and non-crystalline Al and Fe in forest soil was similar to that of savanna, the different soil C:N ratio would cause different availability of P between the vegetation types, although the mechanism is unclear. These results indicate that savanna vegetation is N-limited and forest vegetation is N-saturated (and possibly P-limited) in this zone. We also found that, at 20 cm soil depth, total soil potassium (K) in forest was 1590 kg ha ⁻¹, which was 930 kg ha ⁻¹ less than that in savanna (2520 kg ha ⁻¹; P < 0.05), although a similar difference was not measured for Na, Ca, and magnesium (Mg). Because we observed lower soil pH in forest, not only plant K uptake but also K leaching loss would contribute to lower soil K in forest.</abstract><cop>Kyoto</cop><pub>Taylor & Francis</pub><doi>10.1080/00380768.2013.866523</doi><tpages>15</tpages></addata></record> |
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subjects | aluminum bulk density calcium carbon carbon nitrogen ratio cation exchange capacity clay fraction climate change forest soils Forest-savanna transition zone forests fractionated phosphorus iron leaching magnesium minerals nitrogen Oxisols phosphorus potassium savannas sodium sodium hydroxide soil C:N ratio soil density soil depth soil minerals soil nutrients soil pH soil profiles soil sampling soil texture |
title | Effect of vegetation on soil C, N, P and other minerals in Oxisols at the forest-savanna transition zone of central Africa |
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