蔗糖改性纳米铁原位反应带对硝基苯污染的模拟修复研究

在一维模拟装置中创建改性纳米铁原位反应带,研究反应带对硝基苯污染的修复情况,并通过反应带渗透性变化对其可持续修复能力进行评估.模拟试验结果表明:不同条件下硝基苯的去除率为45%~80%;反应带渗透性变化过程按时间分为3个阶段,分别是0~10d的快速下降期、10~30d的缓慢下降期和30~60d的稳定期,平均下降了53.2%,堵塞现象未发生,反应带可持续修复能力较好.较大的介质粒径和浆液浓度使污染物降解效率增加,硝基苯去除率可分别提高23.7%和13.7%;较高的地下水流速和污染物浓度不利于污染物的去除,硝基苯去除率均下降约46.8%.各反应带中实际参与反应的铁与硝基苯的物质的量比值分别为11.2、17.9、12.6、3.3和25.7,改性纳米铁颗粒的实际利用率较低,实际应用中浆液需要过量注入.     

取代脲类除草剂光催化降解动力学比较

为研究取代脲类除草剂在TiO₂光催化降解过程中的动力学规律,以非草隆、异丙隆和利谷隆3种取代脲类除草剂为研究对象,通过Langmuir-Hinshelwood动力学模型对其TiO₂光催化降解动力学进行模拟,并系统探讨了催化剂用量、C₀(取代脲类除草剂的初始浓度)、溶液pH、温度、ROSs(活性氧物种)和电子捕获剂等的影响. 结果表明:非草隆、异丙隆和利谷隆的TiO₂光催化降解均符合假一级动力学模型,其动力学常数分别为0.082 8、0.068 7和0.095 4 min-1;取代脲类除草剂分子中的芳香环和脲桥上的取代基对降解速率常数的大小有明显的影响. ROSs试验表明,非草隆、异丙隆和利谷隆光催化降解过程中分别有91.6%、95.5%和86.8%的贡献来自·OH;而光生空穴和其他ROSs的贡献相对较小,并且电子捕获剂BrO₃-和S₂O₈2-对取代脲类除草剂的降解动力学有显著的促进作用.      

ZnO纳米粒子通过线粒体通路抑制小鼠光感受器细胞Na~+/K~+-ATP酶表达和活性的作用研究

氧化锌(ZnO)纳米粒子已被发现具有生物毒性,氧化应激被认为是最重要的因素之一。前期实验证实,ZnO纳米粒子能显著减少锰超氧化物歧化酶(Mn SOD)蛋白的表达,降低Mn SOD活性。本文通过检测乳酸脱氢酶(LDH)释放、线粒体活性氧(ROS)水平和膜电位(Δφm)、延迟整流钾电流变化和Na~+/K~+-ATP酶的表达及活性等变化,检测ZnO纳米粒子对小鼠光感受器细胞的细胞毒作用。结果表明,ZnO纳米粒子可显著增强小鼠光感受器细胞中LDH的释放、增加线粒体内ROS水平并下调Δφm、阻断延迟整流钾电流,同时降低Na~+/K~+-ATP酶的表达及活性,从而对小鼠视网膜光感受器细胞产生细胞毒作用,提示ZnO纳米粒子可通过线粒体通路引起氧化应激,从而抑制小鼠光感受器细胞Na~+/K~+-ATP酶表达和活性,产生细胞毒性,导致细胞死亡。本文的研究结果有助于理解ZnO纳米粒子引起细胞毒性的作用机理。     

纳米银的体内毒性及毒作用机制研究进展

很多研究表明纳米银对机体的消化系统、呼吸系统、生殖系统等多个系统均会产生毒作用,且其毒作用受到多种因素的影响。目前关于纳米银的毒作用机制尚未明确,研究发现纳米银的毒作用机制可能与银离子释放、活性氧自由基产生、氧化应激的发生、炎症反应等有关,最新研究指出纳米银的毒性作用还可能与内质网应激和自噬有关,本文将就纳米银的体内毒性及毒作用机制进行了综述。     

增塑剂邻苯二甲酸二异壬酯对雄性小鼠生殖毒性的氧化损伤机制

研究增塑剂邻苯二甲酸二异壬酯(diisononyl phthalate,DINP)对雄性小鼠生殖毒性的氧化损伤机制,以昆明雄性小鼠为受试动物,随机分为7组,包括空白对照组(生理盐水),4个DINP暴露组(0.2、2、20和200 mg·kg~(-1))和褪黑素(melatonin,Mel)对照组50 mg·kg~(-1)、Mel处理组(200 mg·kg~(-1)DINP+50 mg·kg~(-1)Mel),灌胃14 d。以睾丸组织匀浆测定活性氧(ROS)、还原型谷胱甘肽(GSH)和8-羟基脱氧鸟苷(8-OHdG)含量;以睾丸组织细胞测定DNA-蛋白交联(DPC)系数。随着DINP暴露剂量的增加,DINP暴露组睾丸组织ROS、8-OHdG含量和DPC系数逐渐上升,GSH含量逐渐降低,差异有统计学意义(P0.05,P0.01); Mel处理组ROS、8-OHdG含量和DPC系数相应降低,GSH含量逐渐上升。雄性小鼠睾丸组织形态观察结果表明,随着DINP暴露剂量的增加,小鼠睾丸组织的病理损伤程度呈上升趋势。实验结果表明,较高剂量(≥20 mg·kg~(-1))的DINP能造成小鼠睾丸组织的病理损伤和氧化损伤,50 mg·kg~(-1)Mel的抗氧化能力可以有效对小鼠睾丸组织起保护作用,使组织损伤减轻,即生殖毒性减弱。     

热障效应对有顶步行街自然排烟的影响

为了研究热障效应对有顶商业步行街自然排烟的影响,采用理论分析与数值模拟相结合的方法,对不同高度及不同环境温度条件下有顶商业步行街自然排烟时顶棚附近的温度、能见度以及排烟效率进行了分析。结果表明:顶棚附近环境温度越高,自然排烟效果越差,自然排烟效率随顶棚热空气温度的升高呈现线性降低趋势;步行街高度越高,竖直方向的温度差越小,到达顶棚的烟气流速越小,排烟效率越低;当顶棚附近环境温度为45℃时,有顶商业步行街高度不宜超过35 m。     

黄河流域农业生产活性氮排放的时空特征研究

黄河流域是我国的粮食主产区,流域生态保护和高质量发展是当前生态文明建设的核心内容.而活性氮排放是造成水体、大气及气候变化等环境问题的重要因素,已经严重威胁到人类的健康和安全.通过排放因子法对黄河流域2000、2005、2010年农业生产活性氮（Reactive Nitrogen,Nr）排放量进行核算,探讨其时空变动特征.结果表明：①3个年份黄河流域农业生产中活性氮排放总量分别为2185.24、2474.03、2239.96 Gg,其中,N₂O排放量分别为43.95、49.96、48.63 Gg,NH₃排放量分别为615.39、715.08、680.70 Gg,进入到水体的Nr（Nr-wp）排放量分别为1522.01、1704.95、1505.82 Gg,NO_x排放量分别为3.89、4.04、4.82 Gg;②Nr-wp、NH₃、N₂O、NO_x排放占总量的比重分别为67.23%~69.65%、28.16%~30.39%、2.01%~2.17%、0.16%~0.22%;③黄河流域活性氮年平均排放量最高的省份为河南,达到579.40 Gg,其他省份由高到低依次是陕西、山西、山东、甘肃、宁夏、内蒙古、青海、四川,其中,四川的年均排放量最低为94.41 Gg,呈中下游省份排放大于上游省份的分布态势;活性氮排放年均增长率以内蒙古最高,达4.78%,其他省份由高到低依次为宁夏、甘肃、四川、青海、河南、陕西、山东、山西,其中,山西年均增长率最低为-2.57%,年均增长率分布与年均排放量相反,呈中下游省份低于上游省份的格局;④各省份4种形态活性氮排放量的组成与黄河流域整体相似：山西4种形态活性氮排放量均呈下降趋势,山东NH₃、N₂O和Nr-wp排放量有所下降,其他省份均呈增长趋势;Nr-wp、NH₃年均排放量最大和最小的省份均为河南、四川;N₂O、NO_x年均排放量最小的省份均为青海,年均排放量最高的省份分别为河南、山西.通过分析黄河流域农业生产中活性氮排放的时空格局,可为协调黄河流域的人地关系提供科学基础,对黄河流域制定活性氮减排策略具有重要的参考意义.     

应用特殊精馏技术从制药废液中回收四氢呋喃

研究了萃取精馏技术和反应萃取精馏技术在回收四氢呋喃（ＴＨＦ）中的应用,选择了萃取剂和反应萃取剂,设计了工艺流程,优化了操作条件,试验结果表明,采用以上技术从制药废液中回收的ＴＨＦ,纯度可达到９９．４％。     

IMPACT ASSESSMENT MODEL FOR CLEAR WATER FISHES EXPOSED TO EXCESSIVELY CLOUDY WATER1

ABSTRACT: A new type of empirical model described here enables real time assessment of impacts caused by excessive water cloudiness as a function of (a) reduced visual clarity (excessive cloudiness) and (b) duration of exposure to cloudy conditions, in fisheries or fish life stages adapted to life in clear water ecosystems. This model takes the familiar form used in earlier suspended sediment dose effect models where z is severity of ill effect (SEV), x is duration of exposure (h), y is black disk sighting range (y BD, m)—a measure of water clarity, a is the intercept, and b and c are slope coefficients. As calibrated in this study the model is Severity of ill effect is ranked on a 15‐step scale that ranges from 0 to 14, where zero represents nil effect and 14 represents 100 percent mortality. This model, based on peer consultation and limited meta analysis of peer reviewed reports, accomplishes the following: (a) identifies the threshold of the onset of ill effects among clear water fishes; (b) postulates the rate at which serious ill effects are likely to escalate as a function of reduced visual clarity and persistence; (c) provides a context (the “visual clarity” matrix, with its cell coordinates) to share and compare information about impacts as a function of visual clarity “climate” (d) demonstrates changes in predator prey interactions at exposures greater than and less than the threshold of direct ill effects; (e) calibrates trout reactive distance (cm) as function of water clarity in the form where y represents reactive distance (cm) and x represents visual clarity (black disk sighting range, cm), and where a and b are intercept and slope respectively, such that (f) identifies black disk sighting range, in meters, and its reciprocal, beam attenuation, as preferred monitoring variables; and (g) provides two additional optical quality variables (Secchi disk extinction distance and turbidity) which, suitably calibrated as they have been in this study, expand the range of monitoring options in situations in which the preferred technology—beam attenuation equipment or black disk sighting equipment—is unavailable or impractical to use. This new model demonstrates the efficacy of peer collaboration and defines new research horizons for its refinement.     

Oxygen and Water Barrier Properties of Coated Whey Protein and Chitosan Films

Films of whey protein and chitosan acetic acid salt have lower oxygen permeability than, for example, ethylene-co-vinylalcohol under dry conditions, but water and water vapor seriously impair the gas barrier properties. To reduce the oxygen permeability at 90% relative humidity and the water-vapor transmission rate at 100% relative humidity, the films were coated with an alkyd, a beeswax compound, or a nitrocellulose lacquer. Permeability and transmission rate measurements were performed in accordance with standard methods and showed that the beeswax compound and the nitrocellulose were appropriate as water-vapor barriers. Overall migration to water was measured after 10 days exposure time, with the coated surface exposed to the water, showing that the alkyd-coated and the nitrocellulose-coated films were both below the safety limit for food contact. Water absorbency tests, performed by the Cobb method, showed that the films coated with the beeswax compound or with nitrocellulose lacquer exhibit lower absorbency than the alkyd-coated films.