全部 标题 作者
关键词 摘要

OALib Journal期刊
ISSN: 2333-9721
费用:99美元

查看量下载量

相关文章

更多...

Effects of Vegetation Type and Management Practice on Soil Respiration of Grassland in Northern Japan

DOI: 10.1155/2013/624013

Full-Text   Cite this paper   Add to My Lib

Abstract:

Soil respiration rate in two types of grassland dominated with Zoysia japonica and Miscanthus sinensis, respectively, and under two management practices (undisturbed and intentionally burned) for the M. sinensis grassland was investigated for understanding the effects of grassland vegetation type and management practices on the relationship between soil temperature and soil respiration in northern Japan. Soil temperatures at depth of 1 cm in the Z. japonica (ZJ) and burned M. sinensis (MSb) plots had a larger temporal variation than that in the control M. sinensis (MSc) plot prior to early July. However, the coefficient of temperature sensitivity ( ) values, based on soil respiration rates and soil temperatures at 5?cm depth in the ZJ and MSb plots, were 1.3 and 2.9. These rates were lower than that in the MSc plot (4.3), meaning that soil respiration showed lower activity to an increase in soil temperature in the ZJ and MSb plots. In addition, monthly carbon fluxes from soil in these plots were smaller than that in the MSc plot. These results suggested that artificial disturbance would decrease soil microbial or/and plant root respiration, and it would contribute to the plant productivity. Future studies should examine the effects of the intensity and period of management on the soil respiration rate. 1. Introduction Temperate grasslands comprise approximately 16% of the land area in east Asia [1]. In Japan, because the climax vegetation is forest, most grasslands are seminatural or artificial grasslands that require intensive management such as mowing or controlled burning [2]. The area of grassland in Japan is about 387,945?ha, or about 1% of the total land area [3]. The area of controlled burning in Japan is small, with only 0.3% of the total land area burned between April and August in 2000, a typical year [4]. Seminatural and artificial grasslands require continual management by mowing, grazing, or controlled burning. The vegetation types of grasslands differ depending on the strength and frequency of management; for example, Miscanthus sinensis dominated areas are cut once or twice per year, whereas Zoysia japonica dominated areas are cut three times per year [5]. Soil is a major carbon reserve in terrestrial ecosystems, and carbon flux from soil (soil respiration) is an important component because of the second largest carbon flux from the ecosystems. In particular, soil temperature would vary with changes in management type [6, 7], and it would influence soil respiration rate. For instance, many studies around the world reported that land use

References

[1]  T. Oikawa and A. Ito, “Modeling carbon dynamics of terrestrial ecosystem in monsoon Asia,” in Present and Future of Modeling Global Environmental Change: Towards Integrated Modeling, T. Matsuno and H. Kida, Eds., pp. 207–219, Terra Scientific, Tokyo, Japan, 2001.
[2]  M. Kamada and N. Nakagoshi, “Influence of cultural factors on landscapes of mountainous farm villages in Western Japan,” Landscape and Urban Planning, vol. 37, no. 1-2, pp. 85–90, 1997.
[3]  Ministry of Agriculture, Forestry and Fisheries, “Report on results of 2005 census of Agriculture and Forestry in Japan,” Tokyo, Japan, 2005.
[4]  K. Tansey, J.-M. Grégoire, E. Binaghi et al., “A global inventory of burned areas at 1 km resolution for the year 2000 derived from spot vegetation data,” Climatic Change, vol. 67, no. 2-3, pp. 345–377, 2004.
[5]  K. Asami, T. Hattori, and H. Akamatsu, “A study on management by cutting of the embankment vegetation,” The Japanese Institute of Landscape Architecture, vol. 58, no. 5, pp. 125–128, 1995.
[6]  L. N. Kobziar and S. L. Stephens, “The effects of fuels treatments on soil carbon respiration in a Sierra Nevada pine plantation,” Agricultural and Forest Meteorology, vol. 141, no. 2–4, pp. 161–178, 2006.
[7]  M. Bahn, M. Rodeghiero, M. Anderson-Dunn et al., “Soil respiration in European grasslands in relation to climate and assimilate supply,” Ecosystems, vol. 11, no. 8, pp. 1352–1367, 2008.
[8]  F. García-Orenes, A. Cerdà, J. Mataix-Solera et al., “Effects of agricultural management on surface soil properties and soil-water losses in eastern Spain,” Soil & Tillage Research, vol. 106, no. 1, pp. 117–123, 2009.
[9]  F. García-Orenes, C. Guerrero, A. Roldán et al., “Soil microbial biomass and activity under different agricultural management systems in a semiarid Mediterranean agroecosystem,” Soil & Tillage Research, vol. 109, no. 2, pp. 110–115, 2010.
[10]  A. Fterich, M. Mahdhi, and M. Mars, “The effects of Acacia tortilis subsp. raddiana, soil texture and soil depth on soil microbial and biochemical characteristics in arid zones of Tunisia,” Land Degradation & Development, 2011.
[11]  A. C. Campos, J. B. Etchevers, K. L. Oleschko, and C. M. Hidahgo, “Soil microbial biomass and nitrogen mineralization rates along an altitudinal gradient on the Cofre de Perote Volcano (Mexico): the importance of landscape position and land use,” Land Degradation & Development, 2012.
[12]  R. Guénon, M. Vennetier, N. Dupuy, S. Roussos, A. Pailler, and R. Gros, “Trends in recovery of Mediterranean soil chemical properties and microbial activities after infrequent and frequent wildfires,” Land Degradation & Development, vol. 24, pp. 115–128, 2013.
[13]  A. N. Oo, C. B. Iwai, and P. Saenjan, “Soil properties and maize growth in saline and nonsaline soils using cassava-industrial waste compost and vermicompost with or without earthworms,” Land Degradation & Development, 2013.
[14]  R. L. F. Vasconcellos, J. A. Bonfim, D. Baretta, and E. J. B. N. Cardoso, “Arbuscular mycorrahizal fungi and glomalin-related soil protein as potential indicators of soil quality in a recuperation gradient of the Atlantic forest in Brazil,” Land Degradation & Development, 2013.
[15]  J. P. Wu, Z. F. Liu, Y. X. Sun, L. X. Zhou, Y. B. Lin, and S. L. Fu, “Introduced Eucalyptus urophylla plantations change the composition of the soil microbial community in subtropical China,” Land Degradation & Development, vol. 24, pp. 400–406, 2013.
[16]  S. Jaiarree, A. Chidthaisong, N. Tangtham, C. Polprasert, E. Sarobol, and S. C. Tyler, “Carbon budget and sequestration potential in a sandy soil treated with compost,” Land Degradation & Development, 2011.
[17]  T. B. Bruun, B. Elberling, A. de Neergaard, and J. Magid, “Organic carbon dynamics in different soil types after conversion of forest to agriculture,” Land Degradation & Development, 2013.
[18]  N. Liang, T. Nakadai, T. Hirano et al., “In situ comparison of four approaches to estimating soil CO2 efflux in a northern larch (Larix kaempferi Sarg.) forest,” Agricultural and Forest Meteorology, vol. 123, no. 1-2, pp. 97–117, 2004.
[19]  Y. Yazaki, S. Mariko, and H. Koizumi, “Carbon dynamics and budget in a Miscanthus sinensis grassland in Japan,” Ecological Research, vol. 19, no. 5, pp. 511–520, 2004.
[20]  W. Mo, M.-S. Lee, M. Uchida et al., “Seasonal and annual variations in soil respiration in a cool-temperate deciduous broad-leaved forest in Japan,” Agricultural and Forest Meteorology, vol. 134, pp. 81–94, 2005.
[21]  H. Shibata, T. Hiura, Y. Tanaka, K. Takagi, and T. Koike, “Carbon cycling and budget in a forested basin of Southwestern Hokkaido, Northern Japan,” Ecological Research, vol. 20, no. 3, pp. 325–331, 2005.
[22]  M.-S. Lee, J.-S. Lee, and H. Koizumi, “Temporal variation in CO2 efflux from soil and snow surfaces in a Japanese cedar (Cryptomeria japonica) plantation, central Japan,” Ecological Research, vol. 23, no. 4, pp. 777–785, 2008.
[23]  D. Dhital, Y. Yashiro, T. Ohtsuka, H. Noda, Y. Shizu, and H. Koizumi, “Carbon dynamics and budget in a Zoysia japonica grassland, central Japan,” Journal of Plant Research, vol. 123, no. 4, pp. 519–530, 2010.
[24]  T. Ohtsuka, Y. Shizu, A. Nishiwaki, Y. Yashiro, and H. Koizumi, “Carbon cycling and net ecosystem production at an early stage of secondary succession in an abandoned coppice forest,” Journal of Plant Research, vol. 123, no. 4, pp. 393–401, 2010.
[25]  T. Inoue and H. Koizumi, “Effects of environmental factors upon variation in soil respiration of a Zoysia japonica grassland, central Japan,” Ecological Research, vol. 27, no. 2, pp. 445–452, 2012.
[26]  G. Cao, Y. Tang, W. Mo, Y. Wang, Y. Li, and X. Zhao, “Grazing intensity alters soil respiration in an alpine meadow on the Tibetan plateau,” Soil Biology and Biochemistry, vol. 36, no. 2, pp. 237–243, 2004.
[27]  S. Mukhopadhyay and S. K. Maiti, “Soil CO2 Flux in grassland, afforested land and reclaimed coalmine overburden dumps: a case study,” Land Degradation & Development, 2012.
[28]  S. Hashimoto, “Q10 values of soil respiration in Japanese forests,” Journal of Forest Research, vol. 10, no. 5, pp. 409–413, 2005.
[29]  M. Schmitt, M. Bahn, G. Wohlfahrt, U. Tappeiner, and A. Cernusca, “Land use affects the net ecosystem CO2 exchange and its components in mountain grasslands,” Biogeosciences, vol. 7, no. 8, pp. 2297–2309, 2010.
[30]  S. Ma, J. Chen, M. North, H. E. Erickson, M. Bresee, and J. Le Moine, “Short-term effects of experimental burning and thinning on soil respiration in an old-growth, mixed-conifer forest,” Environmental Management, vol. 33, no. 1, pp. S148–S159, 2004.
[31]  A. K. Knapp, S. L. Conard, and J. M. Blair, “Determinants of soil CO2 flux from a sub-humid grassland: effect of fire and fire history,” Ecological Applications, vol. 8, no. 2, pp. 760–770, 1998.
[32]  W. Xu and S. Wan, “Water- and plant-mediated responses of soil respiration to topography, fire, and nitrogen fertilization in a semiarid grassland in Northern China,” Soil Biology and Biochemistry, vol. 40, no. 3, pp. 679–687, 2008.
[33]  A. Rey, E. Pegoraro, C. Oyonarte, A. Were, P. Escribano, and J. Raimundo, “Impact of land degradation on soil respiration in a steppe (Stipa tenacissima L.) semi-arid ecosystem in the SE of Spain,” Soil Biology and Biochemistry, vol. 43, no. 2, pp. 393–403, 2011.
[34]  T. Hernández, C. García, and I. Reinhardt, “Short-term effect of wildfire on the chemical, biochemical and microbiological properties of Mediterranean pine forest soils,” Biology and Fertility of Soils, vol. 25, no. 2, pp. 109–116, 1997.
[35]  S. Castaldi, A. de Grandcourt, A. Rasile, U. Skiba, and R. Valentini, “CO2, CH4 and N2O fluxes from soil of a burned grassland in Central Africa,” Biogeosciences, vol. 7, no. 11, pp. 3459–3471, 2010.
[36]  K. Ono, M. Mano, G. H. Han et al., “Environmental controls on fallow carbon dioxide flux in a single-crop rice paddy, Japan,” Land Degradation & Development, 2013.
[37]  T. Y. Ito and S. Takatsuki, “Relationship between a high density of sika deer and productivity of the short-grass (Zoysia japonica) community: a case study on Kinkazan Island, Northern Japan,” Ecological Research, vol. 20, no. 5, pp. 573–579, 2005.
[38]  S. Shimoda, S. Murayama, W. Mo, and T. Oikawa, “Seasonal contribution of C3 and C4 species to ecosystem respiration and photosynthesis estimated from isotopic measurements of atmospheric CO2 at a grassland in Japan,” Agricultural and Forest Meteorology, vol. 149, no. 3-4, pp. 603–613, 2009.

Full-Text

comments powered by Disqus

Contact Us

service@oalib.com

QQ:3279437679

WhatsApp +8615387084133