Nitrogen cycling in monospecific and mixed-species plantations of Acacia mangium and Eucalyptus at 4 sites in Brazil

被引:31
|
作者
Voigtlaender, M. [1 ]
Brandani, C. B. [1 ]
Caldeira, D. R. M. [2 ]
Tardy, F. [1 ,3 ]
Bouillet, J. -P. [1 ,3 ,4 ]
Goncalves, J. L. M. [1 ]
Moreira, M. Z. [5 ]
Leite, F. P. [6 ]
Brunet, D. [4 ]
Paula, R. R. [1 ,7 ]
Laclau, J. -P. [2 ,3 ,4 ]
机构
[1] Univ Sao Paulo, Dept Forest Sci, ESALQ, BR-13418900 Piracicaba, Brazil
[2] Univ Estadual Paulista, Dept Solos & Recursos Ambientais, UNESP, BR-18610300 Botucatu, SP, Brazil
[3] CIRAD, UMR Eco & Sols, F-34398 Montpellier, France
[4] Univ Montpellier, INRA, CIRAD, Eco & Sols,IRD,Montpellier SupAgro, Montpellier, France
[5] Univ Sao Paulo, CENA, Av Centenario 303, BR-13416903 Piracicaba, Brazil
[6] Coordenacao Pesqulsa Florestal, CENIBRA, BR-35196972 Belo Oriente, MG, Brazil
[7] UFES, Dept Forest Sci & Wood, BR-29550000 Jeronimo Monteiro, Brazil
关键词
Organic matter; N-2; fixation; Eucalypt; Litterfall; Nutrition; Tree mixtures; Tropical plantations; N-15; NATURAL-ABUNDANCE; TREE GROWTH; CARBON SEQUESTRATION; ABOVEGROUND BIOMASS; SOIL FERTILITY; FIXING TREES; STAND-LEVEL; FINE-ROOTS; GRANDIS; DYNAMICS;
D O I
10.1016/j.foreco.2018.12.055
中图分类号
S7 [林业];
学科分类号
0829 ; 0907 ;
摘要
Mixing N-fixing trees with eucalypts is an attractive option to improve the long-term soil N status in fast-growing plantations established in tropical soils. A randomized block design was replicated at four sites in Brazil to compare the biogeochemical cycles in mono-specific stands of Eucalyptus (100E) and Acacia mangium (100A) with mixed species plantations in a proportion of 1:1 (50A50E). Our study aimed to assess the effects of introducing A. rnangium trees in Eucalyptus plantations on atmospheric N-2 fixation, N cycling and soil organic matter stocks. Litterfall and soil N mineralization were measured over the last two years of the rotation (4-6 years after planting). Aboveground N accumulation in the trees and C and N stocks in the forest floor and in the top soil were intensively sampled at harvesting age. N-2 fixation rates were estimated using the natural abundance of N-15 as well as by the difference between total N stocks in 100A and 50A50E relative to 100E (accretion method). While the N-15 natural abundance method was unsuitable, the accretion method showed consistently across the four sites that atmospheric N fixation reached about 250 and 400 kg N ha(-1) rotation(-1) in 50A50E and 100A, respectively. Except at one site with high mortality, N contents within trees at harvesting were approximately 40% higher in 100A than in 100E. Mean N contents in litterfall and N mineralization rates were about 60% higher in 100A than in 100E, with intermediate values in 50A50E. The amounts of N in litterfall were much more dependent on soil N mineralization rates for acacia trees than for eucalypt trees. Soil C and N stocks were dependent on soil texture but not influenced by tree species. N budgets over a 6-year rotation were enhanced by about 65 kg N ha(-1) yr(-1) in 100A and 40 kg N ha(-1) yr(-1) in 50A50E relative to monospecific eucalypt plantations. Introducing N-fixing trees in eucalypt plantations might therefore contribute to reducing the need for mineral N fertilization in the long-term.
引用
收藏
页码:56 / 67
页数:12
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