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Effects Of Adding Straw On Enzyme Activity And Nitrogen Dynamics In Brown Soils Under The Freeze-thaw Conditions

Posted on:2024-04-20Degree:MasterType:Thesis
Country:ChinaCandidate:M LiFull Text:PDF
GTID:2543307055490874Subject:Ecology
Abstract/Summary:PDF Full Text Request
Northeast China is an important grain production base in China,located at mid to high latitudes,with significant seasonal freeze-thaw phenomena.Recently the intensification of abnormal precipitation and frequent freeze-thaw in winter caused by global climate change may affect soil ecological processes,especially soil nitrogen(N)transformation processes.Currently,straw returning is an important measure to improve soil fertility,affecting soil environments and soil N fertility levels,but little is known about how straw returning affects the soil N transformation processes under freeze-thaw cycles.Based on the topsoil of typical brown soil areas,we used a laboratory incubation experiment to explore the effects of straw addition(add or not add),initial soil water content(20%、60%、100%),freeze-thaw cycle times(1、3、5、7、9、12、15、18、21、25)on soil enzyme activity,components and dynamics of N.This study will unravel the relationship between soil N dynamics and enzyme activity under freeze-thaw conditions with straw.The main results are as follows:(1)Freeze-thaw,straw addition,and water treatments their interaction showed significant effects on soil urease and sucrase activities(P<0.05).Relative to the control(without freeze-thaw cycles),freeze-thaw cycles significantly reduced soil sucrase activity by 5%,but showed no significant effects on soil urease activity.Relative to the control(without adding straw),straw addition significantly increased soil sucrase and urease activities by 88%and 67%,respectively.Water treatments significantly affected soil enzyme activities under the freeze-thaw conditions.Relative to the 20%water treatment,soil sucrase and urease activities were significantly higher than those under 60%and 100%water treatments;while there was no significant difference in enzyme activity between 60%and 100%water treatments.Soil urease activity significantly decreased with the increase of freeze-thaw cycling times,and soil urease activity is the highest at the first freeze-thaw cycle,while soil sucrase activity showed an overall increasing trend.(2)Freeze-thaw,straw addition,and water treatments and their interaction showed significant effects on soil N components(P<0.05).Relative to the control(without freeze-thaw cycles),freeze-thaw cycles significantly increased soil ammonium N(NH4+),inorganic N(TIN),alkaline N(AN)and easily hydrolyzable organic nitrogen(EHON)by 98%,33%,15%and 96%,respectively.However,freeze-thaw cycles showed no significant effects on soil nitrogen(NO3-).Relative to the control(without adding straw),straw addition under the freeze-thaw cycle significantly decreased soil NH4+and TIN,and increased NO3-and EHON,but exerted no significant effects on soil AN.Water treatments significantly affected soil N components under freeze-thaw cycles.Relative to the 20%water treatment,soil NH4+and TIN were significantly lower than those under 60%and 100%water treatments;soil NO3-,AN and EHON were significantly higher than those under 60%and 100%water treatments.However,there was no significant difference in N components between 60%and 100%water treatments.The correlation relationships between soil N components and soil properties varied greatly under different soil water treatments.The results of variance partitioning showed that soil water treatment and straw addition,as well as their interaction effects,explained a large variance in soil N components.(3)Freeze-thaw,straw addition,and water treatments and their interaction showed significant effects on siol N mineralization rates(P<0.05).Relative to the control(without freeze-thaw cycles),freeze-thaw cycles significantly increased soil ammonification(AMR)and net nitrogen mineralization(NNMR)rates by 81%and86%,respectively.Relative to the control(without adding straw),straw addition significantly decreased soil AMR and NNMR under the freeze-thaw cycles,but significantly increased nitrification rates(NR).Water treatments significantly affected soil N mineralization rates during the freeze-thaw cycles.Relative to the 20%water treatment,soil AMR and NNMR were significantly lower than those under 60%and100%water treatments;soil NR significantly higher than those under 60%and 100%water treatments;there was no significant difference in N mineralization rates between 60%and 100%water treatments.The freeze-thaw cycling times significantly affected the dynamics of soil N.At the first freeze-thaw cycle,the soil AMR and NNMR were the highest,then significantly decreased,and lastly got to a balance.The results of variance partitioning showed that the freeze-thaw cycle times explained the highest variance in the AMR and NNMR.The interactions of straw,soil moisture,and freeze-thaw cycling times explained the largest part of the variance in the NR.These results indicate that the freeze-thaw cycle could have a significant effect on cycling and supply of brown soil N and these effects may related to straw addition and soil water content.The results could provide theoretical reference and practical support for the cropland management of N fertilizers and comprehensive utilization of crop straw in brown soils of Northeatern China.
Keywords/Search Tags:freeze-thaw cycle, straw returning, nitrogen components, nitrogen mineralization, soil enzymes
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