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滴灌苜蓿田间土壤水盐及苜蓿细根的空间分布
引用本文:鲁为华,任爱天,杨洁晶,于磊,马春晖,张前兵. 滴灌苜蓿田间土壤水盐及苜蓿细根的空间分布[J]. 农业工程学报, 2014, 30(23): 128-137
作者姓名:鲁为华  任爱天  杨洁晶  于磊  马春晖  张前兵
作者单位:石河子大学动物科技学院,石河子,832003
基金项目:石河子大学高层次人才引进项目(RCZX201022);国家牧草产业技术体系项目(CARS-35);兵团博士资金专项(2102BB017)。
摘    要:为了明确滴灌苜蓿土壤水、盐运移,细根分布及细根生物量动态,该文对苜蓿进行滴灌和漫灌试验,结果表明,漫灌水分集中在15 cm浅层土壤内且分布均匀,含水率在19.5%~20.5%之间。滴灌水分高值区集中在水平方向距滴头15 cm,深度为40 cm的土层中,含水率达到18.0%~20.0%。漫灌对0~25 cm深度土层盐分淋洗作用明显,土水比1:5土壤水提液的电导率由灌前的0.4~0.5 m S/cm下降到0.3 m S/cm以下;滴灌可使根区盐分下降至0.2 m S/cm,显著低于灌溉初始的盐分含量(P0.05)。与漫灌比较,滴灌苜蓿细根集中分布在水平方向距滴头0~30 cm,垂直深度0~50 cm范围内。生长季各时间节点滴灌细根总量高于漫灌,其平均值分别为211.6和198.3 g/m2。滴灌和漫灌各时间节点细根量表现出明显的波动,其范围分别在193.2~243.6和182.7~219.1 g/m2之间。在整个生长期内,滴灌活根量高于漫灌,且生长前期滴灌死根量变化较漫灌平稳。活细根和死细根之间的周转使得两者呈现出此消彼涨的状态,表明细根具有生长-凋亡-再生长的周期性。该研究可为滴灌技术在苜蓿栽培上的应用提供参考。

关 键 词:灌溉  土壤  盐分  滴灌苜蓿  水盐分布特征  苜蓿细根  空间分布和生物量动态
收稿时间:2014-06-25
修稿时间:2014-11-25

Soil water and salt movement and spatial distribution of fine alfalfa roots under drip irrigation
Lu Weihu,Ren Aitian,Yang Jiejing,Yu Lei,Ma Chunhui and Zhang Qianbing. Soil water and salt movement and spatial distribution of fine alfalfa roots under drip irrigation[J]. Transactions of the Chinese Society of Agricultural Engineering, 2014, 30(23): 128-137
Authors:Lu Weihu  Ren Aitian  Yang Jiejing  Yu Lei  Ma Chunhui  Zhang Qianbing
Affiliation:College of Animal Science and Technology, Shihezi University, Shihezi 832003, China,College of Animal Science and Technology, Shihezi University, Shihezi 832003, China,College of Animal Science and Technology, Shihezi University, Shihezi 832003, China,College of Animal Science and Technology, Shihezi University, Shihezi 832003, China,College of Animal Science and Technology, Shihezi University, Shihezi 832003, China and College of Animal Science and Technology, Shihezi University, Shihezi 832003, China
Abstract:Abstract: Drip irrigation is being effectively used for alfalfa production in arid northwest China. The objectives of this paper were: i) to compare the effects of flood and drip irrigation on the spatial distribution of water and salt; ii) to compare effects of biomass, spatial distribution and dynamics of fine roots of alfalfa on the movement of water and salt in the soil profile under flood and drip irrigation. From May to October 2012, the plot experiments were carried out in Xinjiang Province. Flood irrigation (irrigation quantity is 4 600 m3/hm2) and drip irrigation treatments were set up (irrigation quantity is 4 200 m3/hm2), alfalfa planted in wide-narrow row plantation with a distance of 15 cm + 30 cm + 15 cm between rows. The results showed that soil water in the flood irrigation treatment was concentrated in the upper 15 cm of the soil profile. Furthermore, the soil water content was uniformly distributed across the plots, ranging between 19.5% and 20.5%. In the drip irrigation plots, soil moisture was concentrated in the upper 40 cm of the soil profile and within 30 cm on either side of the emitter of drip irrigation tapes, and the soil water content ranged between 18.0% and 20.0%. Flood irrigation leached salt to below the 30 cm depth. As a result, salinity in the 0-30 cm depth decreased from 0.4-0.5 mS/cm to 0.3 mS/cm or less. Drip irrigation significantly reduced the salinity to 0.2 mS/cm in the root zone. The narrower-deeper-type soil wetting pattern and desalted zone were formed in drip irrigation and alfalfa planted in this area has higher water content and lower salt content than flood irrigation, therefore drip irrigation provides excellent soil environment for alfalfa growth. While wider-shallower-type soil wetting pattern and desalted zone were formed in flood irrigation. Compared with the flood irrigation treatment, fine roots in the drip irrigation treatment were concentrated in the 0-50 cm depth and near to the emitter of drip irrigation tapes. Total fine roots biomass was greater in the drip irrigation treatment (212 g/m2) than that in the flood irrigation treatment (198 g/m2). Fine root biomass fluctuated during the growing season because of regrowth of alfalfa and harvest schedule. Fine root biomass ranged from 193 to 244 g/m2 in the drip irrigation treatment and from 183 g/m2 to 219 g/m2 in the flood irrigation treatment. During the entire growing period, live fine root biomass was greater in the drip irrigation treatment than that in the flood irrigation treatment. Live fine root biomass was fluctuated in flood and drip irrigation obviously, ranged from 73 to 139 g/m2 and 97 to 144 g/m2 respectively, During the early growth stages (from 2nd April to 18th July), the biomass of dead fine roots changed more smoothly in the drip irrigation treatment (ranged from 93 to 101 g/m2) than in the flood irrigation treatment(ranged from 96 to 125 g/m2), but the biomass of dead fine roots in drip irrigation was fluctuated from 72 to 102 g/m2 after 18th July. Biomasses of live and dead fine roots both changed continuously because of rapid turnover of fine roots, first increasing (growth), then decreasing (death and decomposition), and then increasing again (regrowth) . The results indicated that drip irrigation provide suitable soil condition for alfalfa growth by redistribution of soil water and salt, and the model of the wide-narrow row plantation with a distance of 15 cm + 30 cm + 15 cm between rows and drip irrigation is the optimal cultivation pattern of alfalfa.
Keywords:irrigation   soils   salts   drip irrigated alfalfa   character of water-salt spatial distribution   fine roots of alfalfa   spatial distribution and dynamic of biomass
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