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1.
优化施氮对河套灌区氧化亚氮排放和氨挥发的影响 总被引:1,自引:0,他引:1
以河套灌区盐化潮土为研究对象,采用静态暗箱-气相色谱法和通气法研究了4个施肥处理(不施肥(CK)、传统施肥(CON)、优化处理1(OPT1,减氮53.3%)、优化处理2(OPT2,减氮53.3%+硝化抑制剂))对河套灌区玉米农田氧化亚氮(N_2O-N)排放、氨挥发(NH_3-N)损失和玉米产量的影响.结果表明:氮肥减量显著降低了土壤N_2O-N排放和NH_3-N挥发;相比于CON处理,OPT1处理的N_2O-N排放量和NH_3-N挥发量分别降低了45.2%和68.8%(p0.05),但N_2O-N损失氮素比率增加了9.7%(p0.05).施用硝化抑制剂可显著降低土壤N_2O-N排放,与OPT1处理相比,OPT2处理可降低34.6%(p0.05)的N_2O-N排放和41.5%(p0.05)的N_2O-N损失氮素比率,但NH_3-N挥发增加了47.5%(p0.05).OPT1处理显著降低了玉米产量,降幅达22.1%(p0.05),而OPT2处理相对于OPT1处理增产32.9%(p0.05),与传统施肥处理无差异.因此,综合N_2O-N排放、NH_3-N挥发及玉米产量可知,OPT2是较为合理的施肥措施,值得在河套灌区推广. 相似文献
2.
青岛市人为源氨排放清单及分布特征 总被引:2,自引:0,他引:2
通过调查收集各类人为源氨排放活动水平数据,选取合适的排放因子,建立了青岛市2019年人为源氨排放清单,分析了青岛市人为源氨排放贡献特征及分布特征.结果表明,2019年青岛市人为源氨排放总量为28.33×103 t,排放强度为2.51 t·km-2.其中,畜禽养殖是青岛市最主要的排放源,占全市氨排放总量的比例高达77.80%,其次为农田生态系统和废弃物处理,氨排放量分别占全市总量的7.64%和6.87%.2019年,平度市和莱西市氨排放量较高,分别占青岛市氨排放总量的34.18%和26.23%,而市北区和莱西市排放强度较高,分别达到7.26 t·km-2和4.74 t·km-2.从空间分布上,氨排放量较高的镇街主要分布在青岛市北部和西北部,而排放强度较高的镇街则集中在青岛市市区中部和北部地区. 相似文献
3.
互花米草生物炭的添加对土壤吸附三氯生的影响及其机制研究 总被引:1,自引:0,他引:1
互花米草作为入侵物种,在我国沿海分布广泛,对沿海生态造成负面影响.本研究以互花米草资源化利用为出发点,在300℃和600℃下将其热解分别制得BC300和BC600两种生物炭,采用批量平衡法研究了生物炭添加对土壤吸附三氯生(TCS)的影响及其机制.结果表明,BC300内含有未炭化有机质,对TCS的吸附以分配作用为主,有利于对高浓度TCS的吸附;BC600有较大的比表面积,对TCS的吸附以表面吸附为主,有利于对低浓度TCS的吸附.生物炭添加能够促进土壤对TCS的吸附,且吸附量随生物炭添加比例的增加而增加;添加BC300的土壤对TCS的吸附量要显著高于添加BC600的土壤,这主要与生物炭的结构特征及其对土壤p H值的影响有关.因此,添加300℃下制备的互花米草生物炭可以有效地降低土壤中TCS的环境风险,同时也能为护花米草的资源化利用提供一条可行途径. 相似文献
4.
生物炭对盐碱土壤氨挥发的影响 总被引:1,自引:4,他引:1
为探明生物炭对黄河三角洲盐碱土壤氨(NH_3)挥发的影响,通过室内连续培养的方式,先测定改良的通气法对土壤NH_3挥发的回收率,再对比施加肥料颗粒与肥料水溶液对土壤NH_3挥发的影响,最后探究生物炭的种类、添加量及施肥种类对NH_3挥发速率和总量的影响.结果表明,以硫酸铵为氮源进行的NH_3挥发捕集实验,NH_3回收率平均值高达100. 30%.在相同施氮量下,施加尿素水溶液的处理比施加尿素颗粒的处理NH_3挥发减少了60. 29%,施加硫酸铵水溶液的处理比施加硫酸铵颗粒的处理NH_3挥发减少了61. 40%.相较于不添加生物炭只施用硫酸铵水溶液的空白处理,添加0. 5%生物炭且施加生物炭种类为水稻300℃(RB-300)、水稻600℃(RB-600)、棉花300℃(CB-300)和棉花600℃(CB-600)的处理,NH_3挥发总量分别减少了18. 68%、16. 16%、9. 35%和8. 26%,且施肥后2d内NH_3挥发速率最大,占总挥发量的53. 80%~64. 02%.添加生物炭后,NH_3挥发量随生物炭添加量的增加呈现出先降低后增加的趋势.因此,田间施肥前添加少量生物炭并结合水肥一体化管理技术,可以有效地减少NH_3挥发并提高氮肥利用率. 相似文献
5.
利用DPeRS模型估算巢湖流域氨氮和化学需氧量的面源污染负荷 总被引:4,自引:0,他引:4
巢湖作为安徽省重要的饮用水源,其面源污染问题受到广泛关注.本文利用一种基于遥感分布式面源污染计算模型——DPeRS(Diffuse pollution estimation with remote sensing)模型,估算了巢湖流域2010年氨氮(NH+4-N)和化学需氧量(CODCr)面源污染物负荷,并进行污染特征解析,结果表明:1巢湖流域污染物以耗氧有机物为主,2010年产生NH+4-N 1562 t,进入水体800 t;CODCr9×104t,进入水体5×104t.22010年不同月份面源氨氮和CODCr污染负荷均有显著性差异,其中,7—8月氨氮和CODCr污染产生量较高.3空间分布上,氨氮和CODCr污染物主要集中在巢湖流域西北部地区;从区县角度来看,合肥市市辖区面源污染物产生量及入河排放量最大.4污染类型分析结果表明:城镇径流是氨氮最主要的面源污染源,且氨氮污染负荷与城镇人口密度的相关系数达到0.98,氨氮污染负荷与农田氮平衡的相关系数为0.65;而畜禽养殖是CODCr最主要的面源污染源,且CODCr污染产生负荷与畜禽养殖密度之间有显著的空间关联性,其相关系数达到0.91. 相似文献
6.
HCO3-浓度对厌氧氨氧化反应器脱氮效能的影响 总被引:2,自引:1,他引:2
采用序批式生物膜反应器,通过氮去除速率的测定,研究了HCO3-浓度对厌氧氨氧化反应器脱氮效能的影响.结果表明,当HCO3-与NH4+-N进水浓度比值为0.21时,反应器出水pH值大幅升高,抑制了厌氧氨氧化菌活性,使得氮去除速率大幅下降.当其比值为1.13时,反应器内pH能够降低到厌氧氨氧化菌生长所需要的环境,同时,反应器的氮去除速率开始逐步升高.当过量的HCO3-进入反应器后对厌氧氨氧化反应无影响,说明HCO3-对厌氧氨氧化反应器脱氮效能具有重要的影响,对维持反应器pH值与脱氮效能十分重要.在厌氧氨氧化反应器启动过程中HCO3-与NH4+-N进水浓度最佳比值为1.13. 相似文献
7.
南京城市大气氨-铵的高频演化及其气粒转化机制 总被引:1,自引:1,他引:1
本研究于2018年秋季利用在线气体和气溶胶组分监测仪以高时间分辨率连续测定南京市大气中的气体(主要是NH_3)与二次无机气溶胶(主要是NH_4~+、NO_3~-和SO_4~(2-))浓度,借此研究污染和非污染期城市大气NH_3和NH_4~+的演化规律,进而探讨NH_3-NH_4~+气粒转化过程中的化学机制.结果表明,观测期间NH_3和NH_4~+浓度的平均值(±1σ)分别为(15. 3±6. 7)μg·m-3和(11. 3±7. 8)μg·m-3,且日变化在污染和非污染事件中呈现出显著的差异.综合在线观测的NH_3和NH_4~+浓度数据,通过计算潜在源贡献因子,分析了NH_3和NH_4~+的潜在贡献源区在重污染过程受长距离污染传输影响较小,证明城市也是NH_3排放的重要热点地区.进一步分析发现,NH_3-NH_4~+的气粒转化是影响NH_3和NH_4~+日变化的主要驱动因子.具体体现在:低温、高湿(温度在7. 5~12. 5℃,湿度在50%~90%)时,NH_3和NH_4~+的气固转化速度较快,NH_3与酸性物质反应生成更多的NH_4~+,使得(NH4)2SO4和NH4NO3的形成从而导致污染事件的加剧.研究结果有助于厘清城市大气NH_3的来源和转化机制及其对颗粒物的潜在贡献. 相似文献
8.
Soil aggregates were prepared from a bulk soil collected from paddy soil in the Taihu Lake region and aluminum (Al) dissolution, solution pH changes during copper (Cu2 +) sorption were investigated with static sorption and magnetic stirring. Kinetics of Cu2 + sorption and Al dissolution were also studied by magnetic stirring method. No Al dissolution was observed until Cu2 + sorption was greater than a certain value, which was 632, 450, 601 and 674 mg/kg for sand, clay, silt, and coarse silt fractions, respectively. Aluminum dissolution increased with increasing Cu2 + sorption and decreasing solution pH. An amount of dissolved Al showed a significant positive correlation with non-specific sorption of Cu2 + (R2 > 0.97), and it was still good under different pH values (R2 > 0.95). Copper sorption significantly decreased solution pH. The magnitude of solution pH decline increased as Cu2 + sorption and Al dissolution increased. The sand and clay fraction had a less Al dissolution and pH drop due to the higher ferric oxide, Al oxide and organic matter contents. After sorption reaction for half an hour, the Cu2 + sorption progress reached more than 90% while the Al dissolution progress was only 40%, and lagged behind the Cu2 + sorption. It indicated that aluminum dissolution is associated with non-specific sorption. 相似文献
9.
Effect of orchard age on soil nitrogen transformation in subtropical China and implications 总被引:1,自引:0,他引:1
A better understanding of nitrogen transformation in soils could reveal the capacity for biological inorganic N supply and improve the efficiency of N fertilizers. In this study, a 15N tracing study was carried out to investigate the effects of converting woodland to orchard, and orchard age on the gross rates of N transformation occurring simultaneously in subtropical soils in Eastern China. The results showed that inorganic N supply rate was remained constant with soil organic C and N contents increased after converting woodland into citrus orchard and with increasing orchard age. This phenomenon was most probably due to the increase in the turnover time of recalcitrant organic-N, which increased with decreasing soil pH along with increasing orchard age significantly. The amoA gene copy numbers of both archaeal and bacterial were stimulated by orchard planting and increased with increasing orchard age. The nitrification capacity (defined as the ratio of gross rate of nitrification to total gross rate of mineralization) increased following the Michaelis–Menten equation, sharply in the first 10 years after woodland conversion to orchard, and increased continuously but much more slowly till 30 years. Due to the increase in nitrification capacity and unchanged NO3− consumption, the dominance of ammonium in inorganic N in woodland soil was shifted to nitrate dominance in orchard soils. These results indicated that the risk of NO3− loss was expected to increase and the amount of N needed from fertilizers for fruit growth did not change although soil organic N accumulated with orchard age. 相似文献
10.
Xu Bin Gao Naiyun Rui Min Wang Hong Wu Haihui 《Frontiers of Environmental Science & Engineering in China》2007,1(3):350-356
The ozone oxidation of endocrine disruptor bisphenol A in drinking water was investigated. A stainless completely mixed reactor
was employed to carry out the degradation experiments by means of a batch model. With an initial concentration of 11.0 mg/L,
the removal efficiencies of BPA (bisphenol A) could be measured up to 70%, 82%, and 90% when the dosages of ozone were 1,
1.5, and 2 mg/L, respectively. The impacts on BPA degradation under the conditions of different ozone dosages, water background
values, BPA initial concentrations, and ozone adding time were analyzed. The results showed that ozone dosage plays a dominant
role during the process of BPA degradation, while the impact of the contact time could be ignored. UV wavelength scanning
was used to confirm that the by-products were produced, which could be absorbed at UV254. The value of UV254 was observed
to have changed during the ozonation process. Based on the change of UV254, it could be concluded that BPA is not completely
degraded at low ozone dosage, while shorter adding time of total ozone dosage, high ozone dosage, and improvement of dissolved
ozone concentration greatly contribute to the extent of BPA degradation. The effects of applied H2O2 dose in ozone oxidation of BPA were also examined in this study. The O3-H2O2 processes proved to have similar effects on the degradation of BPA by ozone oxidation.
Translated from Environmental Science, 2006, 27(2): 294–299 [译自: 环境科学] 相似文献
11.
12.
To assess the responses of the soil microbial community to chronic ozone (O3), wheat seedlings (Triticum aestivum Linn.) were planted in the field and exposed to elevated O3 (eO3) concentration. Three treatments were employed: (1) Control treatment (CK), AOT40 = 0; (2) O3-1, AOT40 = 1.59 ppm•h; (3) O3-2, AOT40 = 9.17 ppm•h. Soil samples were collected for the assessment of microbial biomass C, community-level physiological profiles (CLPPs), and phospholipid fatty acids (PLFAs). EO3 concentration significantly reduced soil microbial carbon and changed microbial CLPPs in rhizosphere soil, but not in non-rhizosphere soil. The results of the PLFAs showed that eO3 concentrations had significant effects on soil community structure in both rhizosphere and non-rhizosphere soils. The relative abundances of fungal and actinomycetous indicator PLFAs decreased in both rhizosphere and non-rhizosphere soils, while those of bacterial PLFAs increased. Thus the results proved that eO3 concentration significantly changed the soil microbial community function and composition, which would influence the soil nutrient supply and carbon dynamics under O3 exposure. 相似文献
13.
To assess the responses of the soil microbial community to chronic ozone(O_3), wheat seedlings(Triticum aestivum Linn.) were planted in the field and exposed to elevated O_3(e O_3)concentration. Three treatments were employed:(1) Control treatment(CK), AOT40 = 0;(2) O_3-1, AOT40 = 1.59 ppm·h;(3) O_3-2, AOT40 = 9.17 ppm·h. Soil samples were collected for the assessment of microbial biomass C, community-level physiological profiles(CLPPs), and phospholipid fatty acids(PLFAs). EO_3 concentration significantly reduced soil microbial carbon and changed microbial CLPPs in rhizosphere soil, but not in non-rhizosphere soil.The results of the PLFAs showed that e O_3 concentrations had significant effects on soil community structure in both rhizosphere and non-rhizosphere soils. The relative abundances of fungal and actinomycetous indicator PLFAs decreased in both rhizosphere and non-rhizosphere soils, while those of bacterial PLFAs increased. Thus the results proved that e O_3 concentration significantly changed the soil microbial community function and composition, which would influence the soil nutrient supply and carbon dynamics under O_3 exposure. 相似文献
14.
近年来,无机盐尤其是硝酸盐对我国大气PM2.5的贡献日益凸显,而其如何影响颗粒物的重要理化性质尚待深入研究.于2021年1~12月期间,在镇江市开展了连续观测,获得了大气PM2.5中硫酸铵[(NH4)2SO4)]和硝酸铵(NH4NO3)浓度,系统讨论了二者对颗粒物消光、吸湿增长和酸度的影响.结果表明,2021年镇江市ρ[(NH4)2SO4]和ρ(NH4NO3)的年均值分别为(6.5±4.5)μg ·m-3和(15.0±13.3)μg ·m-3,对PM2.5浓度的平均贡献率分别为(20.5±18.2)%和(34.5±18.4)%;PM2.5的总消光系数为(224.5±194.2) Mm-1,其中NH4NO3的贡献率为(40.1±20.9)%,(NH4)2SO4为(19.1±10.8)%;(NH4)2SO4和NH4NO3是PM2.5吸湿增长的主要贡献者,在污染条件下NH4NO3对颗粒物液态水的贡献率为(53.8±13.4)%~(61.6±14.6)%;NH4NO3是未来镇江市能见度和空气质量改善的关键污染物,但削减NH4NO3前体物可能会导致颗粒物酸度增加,尤其对春冬季节颗粒物酸度的影响较为明显.研究结果对理解空气质量变化及二次影响具有重要意义,并对镇江市空气质量的持续改善提供了重要参考. 相似文献
15.
以亚热带区域闽江河口短叶茳芏中、高潮滩湿地为研究对象,于2014年7月至11月进行氮硫增强输入的实验,利用静态箱-气相色谱法测定潮滩湿地中N_2O排放通量,并同步测量相关的环境因子.结果显示,不同潮滩湿地N_2O排放通量对氮硫增强输入的响应存在差异,但总体上看均促进了N_2O的排放.与对照相比,NH_4~+-N输入使中、高潮滩排放通量分别提高了157.97%和236.36%;NO_3~--N输入使中潮滩提高了60.95%,而使高潮滩N_2O排放通量提高了246.77%;SO_4~(2-)-S输入分别使中、高潮滩N_2O通量提高50.68%和87.17%;而N-S复合输入则使中、高潮滩N_2O通量分别增加了84.20%和117.79%.不同的处理组对中、高潮滩的N_2O排放通量的促进作用分别表现为:NH_4~+-NN-SNO_3~--NSO_4~(2-)-S及NO_3~--NNH_4~+-NN-SSO_4~(2-)-S.氮硫增强输入改变了短叶茳芏潮滩湿地N_2O排放通量的变化规律,但除了NH_4~+-N处理对高潮滩N_2O排放通量的影响显著外,其他处理组的影响均未达到显著性水平.中、高潮滩湿地N_2O的排放通量与沉积物温度、含水率具有显著的相关关系,而与电导率相关性不显著.随着全球环境问题的日益严重,系统研究湿地生态系统N_2O排放的机制与规律,对于科学准确的估算全球温室气体排放量具有重要的意义. 相似文献
16.
凤眼莲对富营养化水体硝化、反硝化脱氮释放N2O的影响 总被引:6,自引:0,他引:6
以往有关大型水生漂浮植物消减富营养化水体氮(N)的研究主要侧重于植物对N的吸收效果,而忽略了硝化、反硝化反应途径对水体脱氮的贡献.基于此,本研究中借助具创新性的收集凤眼莲种植水体释放N2O的装置和方法,通过模拟实验研究了凤眼莲对富营养化水体硝化、反硝化脱氮中间产物N2O的影响.结果表明,凤眼莲可以促进富营养化水体的硝化、反硝化、成对硝化-反硝化反应过程,在本实验条件下凤眼莲种植水体在整个培养期内释放的N2O气体浓度累积升高幅度较大,为453~4055 nL·L-1(未加硝化抑制剂处理),通过释放N2O而脱除氮素的量占整个水体N消减量的1.36%,为相应未种植凤眼莲水体的4.31倍.种植凤眼莲水体试验期间释放N2O-N的量与水体氨态氮或硝态氮浓度的变化量均存在显著相关关系(p<0.05),说明N2O释放量受到水体中NH4+、NO3-浓度变化的影响.种植凤眼莲在实验中后期可以增加水体中硝化、反硝化细菌的数量,但其数量远低于凤眼莲根系附着的硝化反硝化细菌.水体中反硝化细菌数量与水体释放N2O浓度之间并无显著相关性,说明种植凤眼莲水体反硝化脱氮释放N2O过程可能主要是由根系共生微生物驱动的. 相似文献
17.
地形和植被会改变水分在土壤中的运移,进而影响土壤中硝态氮(NO_3~--N)的分布,并可能导致对水体污染的差异.在黄土高塬沟壑区黑河流域选取3个样点,采集刺槐林和草地在不同坡位(上、中和下坡位)的6 m深土样,分析了坡位和植被对NO_3~--N迁移的影响,并初步评估了其对地表水及地下水污染的潜在风险.不同坡位及植被条件下,土壤中硝态氮均没有出现累积,在表层土壤达到最大值后逐渐减小.2种植被下NO_3~--N达到稳定时的深度约为200 cm,稳定浓度均为下坡位上坡位中坡位,但在同一坡位的稳定浓度均有草地高于刺槐林的特点,说明坡位及植被覆盖类型均会影响NO_3~--N在土壤中的分布.整个流域地表水NO-3含量枯水期及汛期分别为(6.90±2.10)mg·L~(-1)和(5.84±2.86)mg·L~(-1),而坡地表层土壤(0~20 cm)中可移动态NO_3~-为(29.55±6.59)mg·L~(-1),明显大于地表水中的浓度,很有可能随径流流失造成地表水氮素污染.地下水枯水期和汛期的NO_3~-含量分别为(24.61±23.72)mg·L~(-1)和(15.70±10.78)mg·L~(-1),而坡地深层土壤(200 cm)中NO-3为(0.78±0.16)mg·L~(-1),由于浓度较低,对地下水造成污染的可能性较小. 相似文献
18.
为研究太原地区的大气氮湿沉降时空变化规律,于2016年1月~2017年12月采用雨量器对太原市市中、近郊和远郊三地大气氮湿沉降进行了为期2年的监测。得到市中、近郊、远郊的NO3--N平均浓度为12.9、18.4、1.3 mg/L,NH4+-N平均浓度分别为3.6、2.3、1.6 mg/L。季节变化上看,NH4+-N浓度值四季相对平均,春夏季稍高,而NO3--N浓度变化较大且冬春季浓度值较高。三个采样点大气氮湿沉降量(无机氮)年均沉降量分别为40.0、48.0、14.2 kg/hm2,以近郊的沉降量最高。市中、近郊、远郊的NH4+-N沉降量分别为9.0、5.0、8.2 kg/hm2,占总无机氮湿沉降量的比重分别为22%、11%、57%,NO3--N沉降量分别是31.0、43.0、6.0 kg/hm2,占总无机氮湿沉降量的比重分别为78%、89%、43%。从上可知城市降水中主要以NO3--N沉降为主,农村则以NH4+-N沉降为主。结合市中、近郊、远郊NH4+-N/NO3--N浓度比值分别为0.54、0.30、1.31,充分表明市中和近郊大气氮湿沉降主要来自工业和交通运输源,远郊则来自农业源。另外,市中、近郊月氮湿沉降量与降雨量差异不显著,远郊则达到极显著水平,说明影响市区两点氮湿沉降的因素较为复杂。由以上数据看出市中和近郊氮污染情况比较严重,应根据各自沉降特点予以控制。 相似文献
19.
生物炭和有机肥对华北农田盐碱土N2O排放的影响 总被引:3,自引:0,他引:3
基于山东滨州地区冬小麦-夏玉米轮作大田试验,探究了施用生物炭和有机肥对夏玉米季土壤氧化亚氮(N_2O)排放的影响,为盐碱土壤N_2O增汇减排提供理论依据.试验按照不同处理氮、磷、钾含量相同原则,设置对照CK[N:0.2t·(hm~2·a)~(-1),P_2O_5:0.12 t·(hm~2·a)~(-1),K_2O:0.2 t·(hm~2·a)~(-1)]、C1[5 t·(hm~2·a)~(-1)生物炭]、C2[10 t·(hm~2·a)~(-1)生物炭]、C3[20 t·(hm~2·a)~(-1)生物炭]、M1[7.5 t·(hm~2·a)~(-1)有机肥]、M2[10 t·(hm~2·a)~(-1)有机肥]这6个处理.结果表明,施加生物炭和有机肥对土壤N_2O排放影响趋势基本一致,排放高峰均出现在施肥(基肥和追肥)后,累积排放量占整个生育期排放量的近一半;与CK相比,C1、C2分别降低N_2O排放的45.3%、31.6%,而C3、M1、M2分别增加了17.3%、37.4%、27.6%.施加生物炭和有机肥均会对土壤N_2O排放产生影响,施加生物炭可以降低N_2O排放,而施加有机肥则促进了N_2O排放.因此,生物炭对减少农田N_2O排放具有巨大潜力. 相似文献
20.
常规施肥条件下农田不同途径氮素损失的原位研究:以长江中下游地区夏玉米季为例 总被引:3,自引:1,他引:3
为了解农田常规施肥条件下的不同途径氮素损失特征,本文通过田间原位试验同步研究了长江中下游地区夏玉米生长季氮肥施用后的农田N2O排放、NH3挥发、氮渗漏和地表径流的变化.结果表明,在复合肥为基肥,尿素为追肥,基追肥氮素水平均为150 kg·hm-2的条件下,整个玉米生长季N2O排放系数为3.3%,NH3挥发损失率为10.2%,氮渗漏和地表径流损失率分别为11.2%和5.1%.此外,基肥施用以氮素渗漏损失为主,而追肥氮素损失以氨挥发和渗漏为主,表明不同途径化肥氮素损失主要受氮肥品种影响,玉米季追肥可改用低氨挥发氮肥品种以减少氮素损失. 相似文献