青藏高原农牧业生态风险时空变化特征与分区防控

青藏高原地区是我国重要的生态安全屏障、战略资源储备基地,农牧业是青藏高原涵盖范围最广的产业,明晰其生态风险对实现青藏高原农牧业可持续发展具有重要意义。构建了青藏高原农牧业生态风险评价体系,并以216个县域为评价单元,分析1990—2015年农牧业开发综合生态风险的时空分布及其重心转移规律,并结合区域农牧业开发强度实现农牧业生态风险权衡分区。结果表明：（1）青藏高原综合生态风险总体有上升趋势,呈“东部多核聚集、西部零星散列”的分布格局。（2）风险重心向西北方向移动,风险主趋势方向转为西北—东南走向。（3）青藏高原限制开发区面积占比最大为50.84%,其次为发展预警区与自然恢复区,青藏高原整体农牧业开发强度较高,应在保障高原生态安全屏障功能的情况下减缓农牧业开发。针对区域特征提出农牧业发展方案,以期为青藏高原地区农牧业开发生态风险防范及发展规划提供科学指引。     

Combined treatment of phenolic wastewater by wet air oxidation and activated sludge

Wet air oxidation (WAO) is employed in this work for treating high concentration chemical wastewater containing phenol and/or phenolic compounds. Experimental results indicate that over 90% removal of phenol or phenolic compounds can be efficiently achieved in the WAO process. Despite of the high treatment efficiency of the WAO process, the treated wastewater, however, still retains relatively high chemical oxygen demand (COD) concentration and does not meet the safe discharge standard. Hence further treatment of the WAO treated wastewater by an aerobic biological treatment using acclimatized activated sludge is necessary. It is found in the present studies that the combined process, if appropriately operated, is capable of drastically reducing the COD concentration of the high concentration chemical wastewater to meet the safe discharge requirement. The operating conditions of the combined process are investigated to determine their respective effects on the overall treatment efficiency. The experimental data also indicate that the oxidation reaction can be represented by a first order kinetics in terms of the component or COD concentration. For both single component and multicomponent wastewaters, the WAO process was found to have different activation energy for oxidation below and above 200°C, suggesting possibly different reaction mechanisms between these temperature ranges. The experimental results provided in the present work can provide significant and practical information for optimizing the combined treatment method.     

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Abstract

Three collectives of substances - plastics, plant nutrients, biotoxins - are candidates for monitoring programmes that could keep track of the quality of ocean waters for vital life processes. All three are not subject to systematic surveillance at present. They are each characterized by long residence times in the marine environment, by increasing influx, and by growing evidence of their deleterious impacts on living systems.     

环戊烯臭氧化反应瞬变物种产生机制

大气中烯烃臭氧化反应产物是二次有机气溶胶(SOA)形成的重要前体物. 运用自行组建的低温基质隔离系统研究环戊烯臭氧化反应的瞬变物种产生机制. 采用程序升温方法,将温度从6 K升至115 K,用傅里叶红外光谱仪检测不同温度下生成的活性中间体,并将试验值与理论计算值、文献报道值进行对比,以确定中间体构型. 结果表明:环戊烯臭氧化反应生成的中间体——POZ(初级臭氧化物)、SOZ(二次臭氧化物)和CI(一分子羰基氧化物和一分子醛或酮)被成功检测到. 其中,POZ的特征吸收峰在705和946 cm-1处,对应O—O—O反对称伸缩振动和环变形振动;SOZ特征吸收峰在939 cm-1处,对应C—O伸缩振动;CI的特征吸收峰在1 733和853 cm-1处,分别对应CO伸缩振动和O—O伸缩振动. 据此,环戊烯臭氧化反应遵循Criegee机制. 采用4种量子化学计算方法——B3LYP/6-311++G(d,2p)、B3LYP/6-311++G(3df,3pd)、MP2/aug-cc-pvdz和PW91PW91/6-311++G(3df,3pd),计算POZ、SOZ和CI特征吸收峰的振动频率,其中POZ在705 cm-1处吸收峰的振动频率计算值分别为725、698、703、680 cm-1;SOZ在1 030 cm-1处吸收峰的振动频率计算值分别为1 017、1 018、1 025和993 cm-1;CI在1 733 cm-1处吸收峰的振动频率计算值分别为1 796、1 803、1 732和1 745 cm-1.表明MP2/aug-cc-pvdz计算的特征振动频率与试验值最接近.      

鲍鱼对2种多环芳烃的富集动力学研究

为探究多环芳烃(PAHs)在海洋生物体内富集过程,选择皱纹盘鲍(Haliotis discus hannai)作为受试生物,应用半静态双箱动力学模型,分别考察了3-甲基菲和9,10-甲基蒽2种多环芳烃在皱纹盘鲍体内的富集动力学过程,通过非线性拟合获得鲍鱼对2种多环芳烃的吸收速率常数(K_1)、释放速率常数(K_2)、生物富集因子(BCF),以及平衡状态下鲍鱼体内2种多环芳烃的含量(Cmax)、生物学半衰期(t_(1/2))等动力学参数。结果表明,鲍鱼对9,10-甲基蒽富集动力学参数K_1、K_2、BCF、Cmax、t_(1/2)的平均值分别为4.9437、0.406、13.59、790.03μg·L~(-1)、3.78 d。鲍鱼对3-甲基菲富集动力学参数K_1、K_2、BCF、Cmax、t_(1/2)的平均值分别为2.3023、0.367、5.97、354.37μg·L~(-1)、3.13 d。鲍鱼在不同浓度下对3-甲基菲和9,10-甲基蒽的生物富集过程均符合双箱动力学模型。     

沈阳环境空气臭氧浓度及累积速率时序曲线模拟研究

为了解环境空气臭氧累积规律,利用2017年沈阳市环境空气臭氧浓度数据,统计分析臭氧累积速率,并利用回归方法拟合并优化臭氧浓度及其累积速率的时间序列模型,同时结合气温、风力、臭氧前体物等时序变化情况分析臭氧浓度的影响因素。研究发现:沈阳市臭氧月均浓度年变化、日均浓度年变化以及小时浓度日变化时序曲线均呈现单峰形态;年变化中,6月的臭氧浓度最大,4月臭氧累积速率达到最大值;日变化中,14:00臭氧浓度达到最大值,09:00—11:00臭氧累积速率最大,19:00—20:00臭氧迅速消减。温度、风速同臭氧浓度之间均有较好的正相关性。臭氧前体物二氧化氮、挥发性有机物与臭氧浓度之间均呈明显的负相关性。     

生物质气化发电厂灰渣中微量元素的赋存形态及其析出

分别用Tessier逐级提取形态分离法和模拟酸雨浸提实验,研究了生物质气化发电厂的气化器、淋洗器和旋风分离器底灰中微量元素的赋存形态及其析出规律,探讨了微量元素析出浓度和影响其析出的因素．结果表明,微量元素大部分存在于残渣态,其有机态、Fe-Mn氧化态和碳酸盐结合态的浓度依次减少,可交换态的赋存量极低;元素的析出受浸提液pH值、浸提温度和浸提时间的影响,元素在灰渣颗粒物中的赋存形态及含量的高低也影响元素的释放和析出程度．     

膨润土颗粒吸附剂的制备及废水中铅离子的处理研究

通过振荡吸附实验,研究了膨润土颗粒吸附材料的制备方法及颗粒吸附材料在含铅离子废水中的吸附特性.结果表明,颗粒化的最佳条件为:膨润土颗粒粒径2mm,焙烧温度550℃,焙烧时间1h.在温度25℃、pH值为6、Pb2+初始浓度为50mg/L、吸附剂用量为8g/L、吸附时间为60min时,吸附剂对废水中Pb2+的吸附去除率达90%以上,吸附剂对Pb2+ 的吸附符合Langmuir吸附方程.     

Evaluation of the Biodegradability of Polyvinyl Alcohol/Starch Blends: A Methodological Comparison of Environmentally Friendly Materials

Polyvinyl alcohol (PVA) and starch are both biodegradable polymers. These two polymers can be prepared as biodegradable plastics that are emerging as one of the environmental friendly materials available now. In this study, after reacting with sodium trimetaphosphate (STMP), modified corn starch was blended with PVA in different ratios by a barbender. Test samples were prepared for mechanical and thermal properties measurements. The surface roughness and morphology of fractured surface of the samples were observed by an atomic force microscopy (AFM) and scanning electron microscope (SEM) measurements. Aqueous degradation by enzyme, water absorption and biodegradability behavior were evaluated for the degradability. The biodegradability of these materials was followed by bio-reactivity kinetics models. Results showed that the addition of modified starch could enhance its water uptake. With an addition of 20 wt% of modified starch, the blend had a maximum weight loss during enzymatic degradation. It was found that the degradability was enhanced with the addition of the starch. Analyzing the results of the biodegradability based on the kinetic models, the growth rate of the microorganism was found to be increasing with the increase of the content of starch in the PVA/starch blends in the first order reaction fashion. In our biodegradability analysis, i.e., based on the China national standards (CNS) 14432 regulations, we estimated the decomposition behavior based on the mentioned first order reaction. We found that the PVA/starch blends would take 32.47, 16.20 and 12.47 years to degrade by 70% as their starch content 0, 20 and 40 wt%, respectively.