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Effects Of Biochar Addition On Soil Greenhouse Gases Emission And Nitrogen Transformation In Meadow Of Wugong Mountain

Posted on:2019-04-03Degree:MasterType:Thesis
Country:ChinaCandidate:L Y ZhengFull Text:PDF
GTID:2370330548987742Subject:Soil and Water Conservation and Desertification Control
Abstract/Summary:PDF Full Text Request
The low-altitude?about 1 500 to 1 900 m elevation?and widely-distributed mountain meadow in Wugong Mountain of Jiangxi province,is an important indicative vegetation type for climate change.Mountain meadow soils represent large carbon?C?and nitrogen?N?pools.However,human disturbances and natural factors have made the mountain meadow experienced different degrees of fire during autumn and winter when the herb was withered.In addition,global changes,such as warming and increased N deposition,directly or indirectly affect the health and stability of mountain meadow ecosystems.Therefore,exploring the effect of biochar residue,especially mixed biochar residue,on soil C and N cycle and nutrient fluctuations after fire disturbance in mountain meadow in the context of global warming and increased N deposition,will help us to further understand the response of soil ecosystem of mountain meadow on climate change.We collected mixed soil and its aboveground vegetation from meadow dominant by species Miscanthus sinensis?henceforth"Ms"?and Arundinella hirta?Thunb?.Tanaka?henceforth"Ah"?together in Wugong Mountain meadow.Then aboveground vegetation was pyrolized biochar?450°C,1h?.Four temperature gradients?10,15,20,25°C?levels and two N?NH4NO3?additions(control vs.6 g N m-2)levels were used to simulate warming and increased N deposition,respectively.The addition of biochar?CK,Ms,MIX of Ms and Ah,Ah?were used to simulate residual biochar input after fire.We conducted a laboratory incubation experiment to investigate greenhouse gases carbon dioxide?CO2?,methane?CH4?,and nitrous oxide?N2O?emission rates of soils at days 1,3,8,13,18,23,28,37,46,55,64,75,89,and soil net ammonification,nitrification,and N mineralization rates at day 93.The results showed that:1)biochar addition?Char vs.CK?increased average N2O emission rates/cumulative N2O emissions,decreased average CO2 emission rates/cumulative CO2 emissions,and weakened average CH4 absorption rates/cumulative CH4absorptions.Average N2O emission rates showed a pattern of CK<?Ms=MIX?<Ah.Average CO2 emission rates showed a pattern of CK<?MIX=Ah?,there was no difference among three biochar.Average CH4 absorption rates/cumulative CH4 absorptions showed a pattern of CK>Ms>MIX>Ah.The cumulative N2O emissions showed a pattern of Ah>MIX>CK and MIX=Ms=CK.Average CO2 emissions showed a pattern of CK<MS<?MIX=Ah?.2)N deposition increased average N2O emission rates.3)The temperature sensitivity(Q10)of cumulative N2O emissions showed a pattern of?Ms=MIX=Ah?>CK.Q10 of cumulative CO2 emissions showed a pattern of CK and Ms>Ah,there was no significant difference between mixed biochar and other biochar treatments.4)N deposition showed no significant effect on Q10 of cumulative N2O and CO2 emissions?P>0.05?.5)There was a non-additive effect on the average cumulative soil CO2 and CH4 emissions,the observed values?mixed biochar,MIX?were significantly different from the predicted values?“Ms+Ah”/2??P<0.05?.6)The addition of biochar?Char vs.CK?increased average net nitrification and ammonification rates and decreased average net N mineralization.Average net nitrification rates was higher in CK than other three types of biochar treatments.On the other hand,average net ammonification rates presented negative values and showed a pattern of Ah>MIX>?Ms=CK?.Average net N mineralization rate showed a pattern of Ms<?CK=MIX=Ah?.7)N deposition reduced average net ammonification and N mineralization rates.8)There was a significant positive correlation between soil N2O emissions and soil net nitrification or N mineralization rates?P<0.05?.In conclusion,although the addition of biochar promoted soil N2O emissions,it reduced the Q10 of soil N2O and CO2 emissions,and net nitrification rate.N addition increased soil N2O emissions but decreased soil net ammonification rates and N mineralization rates.Therefore,when predicting the effect of fire disturbance on soil C and N cycle,especially the potential of greenhouse gas emissions in mountain meadow,global climate change,such as climate warming and N deposition must be fully considered.
Keywords/Search Tags:Meadow, Greenhouse gases, Nitrogen deposition, Biochar, Nitrogen mineralization, Q10, Wugong Mountain, Fire disturbance
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