厌氧-Carrousel氧化沟处理亚麻沤制废水的试验研究

亚麻沤制废水是一种高浓度有机废水,经厌氧处理后,出水仍不达标.采用厌氧-Carrousel氧化沟进行后续处理试验,并引进了ACF32微生物制剂进行污泥培养,出水CODCr值在200 mg/L左右,TN值维持在22 mg/L左右,TP值维持在3 mg/L以下,最后讨论了试验中影响处理效果的主要因素.     

乌鲁木齐市一次冷空气过境天气对空气污染的影响分析

根据对2006年11月20～28日乌鲁木齐市出现冷空气过境天气过程的天气形式和主要气象要素及空气污染变化情况进行的分析,结果表明:冷空气过境天气前后,诸多气象要素发生了变化,冷空气导致逆温层的破坏和降水过程使各项污染物均得到有效的清除.通过此分析可为类似天气的空气质量预报提供思路.     

千岛湖水源水微生物安全性评价

千岛湖作为国家战略水源地,其微生物安全直接关系到千万居民的用水安全.为了研究千岛湖湖水的生物安全性,于2018-2019年采集了金竹牌取水口不同深度的水样,并检测了水样的可生物降解溶解性有机碳(BDOC)、细菌再生长的潜力(BGP)、可培养细菌数、潜在的条件致病菌和细菌群落结构.结果显示,千岛湖水质属地表水Ⅱ～Ⅲ类水,...     

不同光照时间对杏鲍菇生长发育的影响

为探究光照时间对杏鲍菇生长发育的影响,设置蓝、白两种光质,每种光质下设置5种不同光照时间处理进行栽培试验,并测定每个处理下杏鲍菇原基形成与分化速度、菇蕾与子实体形态、产量及可溶性蛋白质与总糖含量.结果显示,原基形成速度随光照时间增加呈现先增加后降低的趋势,蓝光下以15 min光照15 min黑暗时间处理下原基形成速度最...     

清江高坝洲津洋口防护区水环境污染治理

介绍了湖北省清江高坝洲津洋口防护区的概况,对津洋口防护区水环境污染现状进行了分析和调查研究,同时得出了防护区的主要污染为工业废水污染.计算了津洋口防护区丹水河的水环境容量,并据此提出水环境污染治理方案.     

湖北长江三峡地区山水林田湖草生态保护修复形势与对策研究

文章重点分析了湖北长江三峡地区生态功能定位、生态保护修复重点,剖析了湖北长江三峡地区山水林田湖草生态保护修复形势,在介绍湖北长江三峡地区山水林田湖草生态保护修复工程试点的基础上,深入分析了该工程试点推进中的难点问题。提出了相应对策：坚持用系统思维推进山水林田湖草整体保护和修复;加强生态环境问题突出区域重点攻坚,着力解决生态保护修复不充分、不平衡问题;加大社会资本、绿色金融支持力度,健全多元化、差异化资金供给及管理机制;积极探索生态产品及废弃资源价值转化新途径;加强科技支撑、坚持自主创新、打造精品示范工程;提升建设项目服务水平,加强生态环境监测及风险应急能力建设。     

Comparison of forest edge effects on throughfall deposition in different forest types

This study examined the influence of distance to the forest edge, forest type, and time on Cl⁻, SO₄²⁻, NO₃⁻, and NH₄⁺ throughfall deposition in forest edges. The forests were dominated by pedunculate oak, silver birch, or Corsican/Austrian pine, and were situated in two regions of Flanders (Belgium). Along transects, throughfall deposition was monitored at distances of 0-128 m from the forest edge. A repeated-measures analysis demonstrated that time, forest type, and distance to the forest edge significantly influenced throughfall deposition of the ions studied. The effect of distance to the forest edge depended significantly on forest type in the deposition of Cl⁻, SO₄²⁻, and NO₃⁻: the edge effect was significantly greater in pine stands than in deciduous birch and oak stands. This finding supports the possibility of converting pine plantations into oak or birch forests in order to mitigate the input of nitrogen and potentially acidifying deposition.     

蒙古冷涡影响下宁夏两次典型冰雹天气对比分析

基于常规气象资料和宁夏中尺度区域数值模式MM5输出结果,应用天气学及诊断分析方法,对2004年6月14日和2005年5月30日发生在宁夏的两次典型冰雹天气过程,从环流背景、影响系统、冰雹落区、大气层结稳定度及动力条件等方面进行了对比分析。结果表明：两次冰雹天气过程均发生在宁夏冰雹易发期夏初季节的午后,是在＂西高东低＂有利于强对流天气发生的环流背景下,受蒙古冷涡影响而形成的。由于环流形势及其演变的不同,使蒙古冷涡移动路径有所差异,造成宁夏不同区域受到冰雹袭击。     

建筑火灾烟流运动特性网络模型的求解收敛性

分析了运用网络模型模拟建筑火灾烟流的计算过程,通过总结影响网络模型求解精度及收敛性的关键因素,改进了原烟流预测软件对建筑物各开口的净、正、负质量流量的算法。改进后的模型消除了振荡效应,模拟结果曲线平滑稳定,实现了运用网络模型对多室建筑物烟流特性的模拟计算。     

Partitioning of hydrogen peroxide between the gas and liquid phases in the presence of surfactant

Gas-liquid phase partitioning is a key physical property that can predict the environmental fate of a compound between two phases. Several environmental factors have been known to affect the gas-liquid phase partitioning. We investigated the influence of surfactant on the gas-liquid phase partitioning of hydrogen peroxide (H(2)O(2)). The surfactant used was ammonium perfluorooctanoate (APFO). H(2)O(2) solution containing the surfactant was equilibrated in a closed system and gas phase H(2)O(2) concentration was measured by the peroxyoxalate chemiluminescence (PO-CL) method. Gas phase H(2)O(2) concentrations remained constant below the critical micelle concentration (CMC) and increased linearly with surfactant concentration above the CMC, which indicated that surfactant micelles influenced the gas-liquid phase partitioning of H(2)O(2). This result showed that H(2)O(2)-micelle interactions are less favorable than H(2)O(2)-H(2)O interactions. Surfactant monomers did not affect the gas-liquid phase partitioning of H(2)O(2) due to the absence of micelles. Solvent (methanol) effect was also investigated and showed that gas phase H(2)O(2) concentrations increased with the addition of solvent. This indicated the unfavorable interaction of H(2)O(2) with hydrophobic medium compared to hydrophilic one. It is consistent with the result that H(2)O(2)-micelles has a weaker interaction than H(2)O(2)-water because surfactant micelles are hydrocarbon-like organic phase rather than aqueous phase.