Eight years of annual no-till cropping in Washington's winter wheat-summer fallow region

The tillage-based winter wheat (Triticum aestivum L.)-summer fallow (WW-SF) cropping system has dominated dryland farming in the Pacific Northwest USA for 125 years. We conducted a large-scale multidisciplinary 8-year study of annual (i.e., no summer fallow) no-till cropping systems as an alternative to WW-SF. Soft white and hard white classes of winter and spring wheat, spring barley (Hordeum vulgare L.), yellow mustard (Brassica hirta Moench), and safflower (Carthamus tinctorius L.) were grown in various rotation combinations. Annual precipitation was less than the long-term average of 301 mm in 7 out of 8 years. Rhizoctonia bare patch disease caused by the fungus Rhizoctonia solani AG-8 appeared in year 3 and continued through year 8 in all no-till plots. All crops were susceptible to rhizoctonia, but bare patch area in wheat was reduced, and grain yield increased, when wheat was grown in rotation with barley every other year. Remnant downy brome (Bromus tectorum L.) weed seeds remained dormant for 6 years and longer to heavily infest recrop winter wheat. There were few quantifiable changes in soil quality due to crop rotation, but soil organic carbon (SOC) increased in the surface 0–5 cm depth with no-till during the 8 years to approach that found in undisturbed native soil. Annual no-till crop rotations experienced lower average profitability and greater income variability compared to WW-SF. Yellow mustard and safflower were not economically viable. Continuous annual cropping using no-till provides excellent protection against wind erosion and shows potential to increase soil quality, but the practice involves high economic risk compared to WW-SF. This paper provides the first comprehensive multidisciplinary report of long-term alternative annual no-till cropping systems research in the low-precipitation region of the Pacific Northwest.     

重点生态功能区环境污染源排放特征与空间管控模式——以藏东南为例

重点生态功能区以保持并提高生态产品供给能力为主体功能定位，区内自然环境敏感性和脆弱性突出，研究其人类活动过程中的环境污染源排放特征与空间管控模式，对科学协调保护与利用、切实加强重点生态功能区环境保护和治理水平具有重要意义.以青藏高原重要生态安全屏障区藏东南为例，基于环境污染源的固体废弃物、水体污染物和大气污染物排放强度的分类估算与空间特征解析，探讨面向污染源排放强度和多尺度管控精度的分级空间管控方案.研究结果表明：藏东南环境污染源的排放强度整体较低，雅鲁藏布江和雅尼河谷地因人类生产生活活动密度较大，其污染物排放量显著高于其他区域；在重点生态功能区应建立由7个二级类和21个三级类构成的环境污染源空间管控体系，重点管控以城镇居住区和工矿业生产空间为主的"点状"胁迫、以交通运输场所和人文游憩空间为主的"线状"胁迫、以农业种植区和畜禽养殖区为主的"面状"胁迫；针对藏东南各类环境污染源的空间耦合及交互特征，提出城乡生活集聚型、农牧业生产集聚型和休闲旅游集聚型3种典型区，依次制定"分级处理+资源利用"、"源头减排+就地消纳"、"实时动态监控+绿色设施营造+游憩利用规范"的差异化空间管控模式.     

亩强度Te（Ⅳ）胁迫对极大螺旋藻生理生化性质的影响

对极大螺旋藻（Spirulina maxima）在接种后第3～5d分3次添加Na2TeO3，4个Te胁迫组的累计加Te量分别为650、750、850和950mg／L。结果表明：4个Te胁迫组螺旋藻的最终生物量、水溶性蛋白、藻蓝蛋白和别藻蓝蛋白的含量均低于对照组，且随Te胁迫强度增加而逐渐减少；而SOD的比活力均高于对照组，但随Te胁迫强度增加也呈逐渐减少趋势；Te（Ⅳ）胁迫没有改变螺旋藻中脂溶性色素的组成，但各色素的含量也随Te胁迫强度增加而下降；胞外多糖含量随Te胁迫强度增加而增加，但950mg／L实验组（第9dxTe（Ⅳ）为2．21），胞外多糖的含量反而下降。     

光照、温度和营养盐对滇池微囊藻生长的影响

研究了光照、温度与营养盐对滇地铜绿微囊藻（Ｍｉｃｒｏｃｙｓｔｉｓａｅｒｕｇｉｎｏｓａ）生长的影响。实验表明，在５００～５０００ｌｘ光强范围内，随光强增加，比增殖速率加大；在２２～３５℃区间内，比增殖速率随温度的升高而增加，且温度的影响大于光照；氮磷比（Ｎ／Ｐ）值在５～１０范围内，比增殖速率变化较大，Ｎ／Ｐ值为１４．５时，比增殖速率达最大值。滇池湖水的氮磷比值为１４．４左右，与实验值相接近。根据实验结果及限制因子的定义，总体上讲，滇池中磷是藻类生长的主要限制因子，控制滇池富营养化应以控制磷为主。     

沸石曝气生物滤池去除氨氮性能及生物学特征分析

天然沸石具有较大的孔隙率和比表面积,对氨氮有较强的选择性离子交换能力.运用天然沸石曝气生物滤池处理城市污水厂二级生化出水,结果表明,曝气生物滤池有良好的去除效果.在气水比为3∶1,水力负荷为1 m/h,温度＞20℃情况下,沸石曝气生物滤池对城市污水厂二级生化出水COD去除率为12.7%,NH3-N去除率为96.6%;试验系统沿程微生物活性和微生物量呈现逐渐下降趋势,而单位生物量的生物活性沿程分布则与此相反;曝气生物滤池对水中污染物的去除主要集中在底部进水端部分,当水流达到距进水端上方105 cm时,曝气生物滤池对水中NH3-N的去除率已达86.8%(占氨氮总去除率的90%),COD的去除率为13.3%(占COD总去除率的67%).     

人为干扰对川西亚高山针叶林土壤物理性质的影响

研究了川西亚高山针叶人工林在几种不同强度人为干扰下林地土壤物理性质。结果表明，随人为干扰强度的增加，土壤中细土（粉粒、粘粒）和大团聚体数量减少，小团聚体和原生土壤颗粒增加；土壤表层孔隙度减小，尤其是大孔隙明显减少；土壤有效水降低，持水供水能力减弱，渗透系数减小。川西亚高山人工针叶林土壤生态功能随人为干扰强度的增加而减弱，建议在最易受人为干扰的造林地区，最好是在造林初期封山育林。图1表5参13     

不同放牧强度下星毛委陵菜(Potentilla acaulis)种群小尺度空间格局

利用R ip ley’s K函数以及蒙特卡罗(Monte Carlo)随机模拟方法,定量分析了4种放牧强度———无牧、轻牧(1.33只羊/hm2)、中牧(4.00只羊/hm2)、重牧(6.67只羊/hm2)下星毛委陵菜(Potentilla acaulis)种群的小尺度空间格局及其随尺度的变化规律;研究了放牧对星毛委陵菜种群空间格局的影响;并以放牧条件下星毛委陵菜的生活史特征、生态适应对策以及群落内植物种间的相互作用为基础,探讨产生和维持这些格局的机理.研究表明:(1)放牧对星毛委陵菜种群空间格局有显著影响,同一放牧强度下星毛委陵菜种群在不同尺度上的空间格局存在显著差异.(2)无牧条件下,星毛委陵菜种群在0~96 cm尺度上表现为集聚分布,在96~100 cm尺度为随机分布;轻牧条件下,星毛委陵菜种群在0~92 cm尺度上表现为集聚分布,在92~100 cm尺度为随机分布;中牧条件下,星毛委陵菜种群在0~72cm尺度上表现为集聚分布,在72~100 cm尺度为随机分布;重牧条件下,星毛委陵菜在20~22 cm尺度上表现为集聚分布,在15~17 cm、23~28 cm和46~50 cm尺度为均匀分布,在0~15 cm、17~20 cm、22~23 cm、28~46 cm和50~100 cm上为随机分布.(3)同一放牧强度下,随着尺度的增大,星毛委陵菜种群由集聚分布趋向于随机分布;且转变为随机分布时的尺度随着放牧强度的增大而逐渐缩小.这与星毛委陵菜生物学特性和种群对放牧压力的生态适应对策密切相关.(4)在0~100 cm尺度上,星毛委陵菜种群的集聚强度随着放牧强度的增大而逐渐减小,即:无牧>轻牧>中牧>重牧.(5)放牧活动改变了决定群落结构的有关过程的相对重要性.这些研究结果将为在放牧活动干扰下草原群落的演替提供理论依据.图2参24     

室内废气污染的计算与分析

通过对吸油烟机抽吸风场有效强度矢量图的测量 ,给出了吸油烟机质量技术检验方法和油烟废气、燃气废气污染泄漏量的计算方法 ;对油烟、燃气废气在厨房的扩散与循环作了详细分析 ,并对国标提出几点建议。     

Origins of black carbon from anthropogenic emissions and open biomass burning transported to Xishuangbanna, Southwest China

Black carbon (BC) has importance regarding aerosol composition, radiative balance, and human exposure. This study adopted a backward-trajectory approach to quantify the origins of BC from anthropogenic emissions ($\mathrm{B}{\mathrm{C}}_{\text{An}}$) and open biomass burning ($\mathrm{B}{\mathrm{C}}_{\text{BB}}$) transported to Xishuangbanna in 2017. Haze months, between haze and clean months, and clean months in Xishuangbanna were defined according to daily PM_2.5 concentrations of >75, 35–75, and <35 µg/m³, respectively. Results showed that the transport efficiency density (TED) of BC transported to Xishuangbanna was controlled by the prevailing winds in different seasons. The yearly contributions to the effective emission intensity of $\mathrm{B}{\mathrm{C}}_{\text{An}}$ and $\mathrm{B}{\mathrm{C}}_{\text{BB}}$ transported to Xishuangbanna were 52% and 48%, respectively. However, when haze occurred in Xishuangbanna, the average $\mathrm{B}{\mathrm{C}}_{\text{An}}$ and $\mathrm{B}{\mathrm{C}}_{\text{BB}}$ contributions were 23% and 77%, respectively. This suggests that open biomass burning (BB) becomes the dominant source in haze months. Myanmar, India, and Laos were the dominant source regions of BC transported to Xishuangbanna during haze months, accounting for 59%, 18%, and 13% of the total, respectively. Furthermore, India was identified as the most important source regions of $\mathrm{B}{\mathrm{C}}_{\text{An}}$ transported to Xishuangbanna in haze months, accounting for 14%. The two countries making the greatest contributions to $\mathrm{B}{\mathrm{C}}_{\text{BB}}$ transported to Xishuangbanna were Myanmar and Laos in haze months, accounting for 55% and 13%, respectively. BC emissions from Xishuangbanna had minimal effects on the results of the present study. It is suggested that open BB in Myanmar and Laos, and anthropogenic emissions in India were responsible for poor air quality in Xishuangbanna.     

Effect of organophosphorus pesticide pollution on soil animals

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