首页 | 本学科首页   官方微博 | 高级检索  
文章检索
  按 检索   检索词:      
出版年份:   被引次数:   他引次数: 提示:输入*表示无穷大
  收费全文   2篇
  免费   0篇
  国内免费   10篇
安全科学   1篇
综合类   2篇
污染及防治   9篇
  2022年   1篇
  2017年   1篇
  2014年   1篇
  2013年   5篇
  2012年   3篇
  2010年   1篇
排序方式: 共有12条查询结果,搜索用时 15 毫秒
1.
本实验以工业化学合成聚合硫酸铁混凝剂和自制生物聚合硫酸铁为例,考察了铁系混凝剂品种对地表水浊度、TOC和UV254的去除效果,混凝剂品种对混凝-超滤联合工艺处理地表水过程中超滤膜污染的影响。混凝实验结果表明,在10 mg/L(以Fe3+计)最佳投加量下,两类混凝剂对浊度、TOC和UV254的去除率基本相同。超滤膜污染实验结果表明,生物聚合铁预处理水样通量衰减速度略大于化学聚合铁预处理水样;膜污染阻力分析结果显示,随着循环次数的增加,工业化学合成聚合铁预处理水样造成的不可逆污染阻力逐渐增加,而生物聚合铁预处理水样造成的不可逆污染阻力却略有下降;膜污染机理分析表明,2组过滤过程的膜污染类型基本相似,由最初的膜孔堵塞过渡到最终的滤饼层污染。SEM分析表明,生物聚合铁预处理水样的膜污染较为严重。  相似文献   
2.
采用海水和盐田水作为驱动液,研究正渗透过程中的通量变化和膜污染特征,探索其作为驱动液的可行性。结果表明,海水和盐田水含有大量的盐离子,具有高的渗透压,海水、2#、5#和9#盐田水与0.42、0.8、2.2和4.2 mol/L的氯化钠具有同样的通量行为。随海水和盐田水浓度增加,通量增加,同时污染也越严重。扫描电子显微镜观察和荧光光谱分析发现,盐田水中的硅酸盐和有机物会沉积在膜表面,引起比较严重的膜污染,尤其是高浓度的盐田水。海水和盐田水作为正渗透过程中的驱动液需要进行一定的预处理。  相似文献   
3.
城市污水厂污泥化学调理深度脱水机理   总被引:3,自引:0,他引:3  
城市污水厂剩余污泥脱水是当前实际生产中亟待解决的问题。考察了厦门市集美污水厂剩余污泥经FeCl3和CaO,投加量分别为污泥质量分数的0.5%~0.7%和1.0%~1.5%化学调理前后污泥粒度、形态及胞外聚合物(extracellular polymeric substances,EPS)的变化。结果表明,调理后污泥比阻降低86%,污泥颗粒之间细碎紧密,细菌表面变得粗糙,经板框压滤后含水率低于60%。由三维荧光光谱(three-dimensional emission and excitation matrixs,EEM)光谱分析可知,LB-EPS(loosely bound-EPS)同TB-EPS(Tightly bound-EPS)的荧光峰整体发生红移,出现位于IV区域的色氨酸类蛋白质荧光峰Ex/Em=313/380 nm。FeCl3和CaO的加入一方面破坏了污泥颗粒的细胞结构,使EPS大量溶出,细胞结合水变成表面吸附水;另一方面Fe3+和CaO水解,中和污泥负电荷,通过压缩双电层作用破坏污泥胶体颗粒的稳定,去除表面吸附水,大幅提高了污泥的脱水性能,利于进一步板框压滤脱水。  相似文献   
4.
热解温度和时间对生物干化污泥生物炭性质的影响   总被引:5,自引:0,他引:5  
污泥热解制备生物炭是一种很有潜力的污泥资源化处置方式,然而,生物炭产量和品质因污泥原料性质、热解条件(如热解温度、时间)的不同而存在显著差异。以生物干化污泥为主要研究对象,系统考察了热解温度及时间等热解因素对生物炭品质的影响。实验结果表明,随着热解温度的升高(300~700℃),热解时间的增加(2~4 h),生物炭产率均下降。低温热解(300℃)生物炭,偏酸性,而高温热解时(700℃)生物炭,偏碱性。生物炭N含量随着热解温度的升高、热解时间的增加而降低,而P、K及微量元素随着热解温度的升高,热解时间的增加而增加。DTPA浸提结果表明,高温热解明显降低了生物炭中微量元素的生物有效性。  相似文献   
5.
随着我国城市化和工业化进程的快速推进,城市建设产生大量的建筑废弃物,燃煤电厂产生大量炉底渣,建筑固废的处置在城市可持续发展过程中备受关注。以建筑垃圾再生骨料、炉底渣和石粉等区域特色的骨料制备环保砖,系统考察了骨料对环保砖力学性能的影响。实验结果表明,再生骨料的种类对环保砖抗压强度的影响显著。再生骨料中混凝土的增加,环保砖抗压强度逐渐增加;而再生骨料中粘土砖含量的增加,环保砖抗压强度明显降低。环保砖抗压强度随炉底渣的含量增加而降低,石粉对环保砖抗压强度有提升作用。  相似文献   
6.
The presence of SO2 display significant effect on the mercury (Hg) adsorption ability of carbon-based sorbent. Yet the adsorption and oxidation of SO2 on carbon with oxygen group, as well as the roles of different sulfur oxide groups in Hg adsorption have heretofore been unclear. The formation of sulfur oxide groups by SO2 and their effects on Hg adsorption on carbon was detailed examined by the density functional theory. The results show that SO2 can be oxidized into SO3 by oxygen group on carbon surface. Both C-SO2 and C-SO3 can improve Hg adsorption on carbon site, while the promotive effect of C-SO2 is stronger than C-SO3. Electron density difference analyses reveal that sulfur oxide groups enhance the charge transfer ability of surface unsaturated carbon atom, thereby improving Hg adsorption. The experimental results confirm that surface active groups formed by SO2 adsorption is more active for Hg adsorption than the groups generated by SO3.  相似文献   
7.
以粉煤灰为主要原料制备多孔陶粒,并在其上负载水合氧化钛以制备吸磷材料.研究结果表明,陶粒吸磷主要通过其中羟基和磷酸根的离子交换实现.在40℃,pH值为10时对磷酸根有较好的吸附能力,饱和吸附量为7.8 mg/g.吸附等温线符合Lngmiur吸附模型,吸附动力学符合二级吸附动力学模型.吸附后的滤料可在NaOH中再生,经多次“吸附-解吸”后,其吸附容量可达到1.35 mg/g左右.  相似文献   
8.
The pollutants in urban storm runoff,which lead to an non-point source contamination of water environment around cities,are of great concerns.The distributions of typical contaminants and the variations of their species in short term storm runoff from different land surfaces in Xiamen City were investigated.The concentrations of various contaminants,including organic matter,nutrients(i.e.,N and P) and heavy metals,were significantly higher in parking lot and road runoff than those in roof and lawn runoff.The early runoff samples from traffic road and parking lot contained much high total nitrogen(TN 6-19 mg/L) and total phosphorus(TP 1-3 mg/L).A large proportion(around 60%) of TN existed as total dissolved nitrogen(TDN) species in most runoff.The percentage of TDN and the percentage of total dissolved phosphorus remained relatively stable during the rain events and did not decrease as dramatically as TN and TP.In addition,only parking lot and road runoff were contaminated by heavy metals,and both Pb(25-120 μg/L) and Zn(0.1-1.2 mg/L) were major heavy metals contaminating both runoff.Soluble Pb and Zn were predominantly existed as labile complex species(50%-99%),which may be adsorbed onto the surfaces of suspended particles and could be easily released out when pH decreased.This would have the great impact to the environment.  相似文献   
9.
Liu  Hui  Xiang  Kaisong  Yang  Bentao  Xie  Xiaofeng  Wang  Dongli  Zhang  Cong  Liu  Zhilou  Yang  Shu  Liu  Cao  Zou  Jianping  Chai  Liyuan 《Environmental science and pollution research international》2017,24(16):14249-14258

Converting the NO from gaseous pollutant into NH4 + through electrocatalytical reduction using cost-effective materials holds great promise for pollutant purifying and resources recycling. In this work, we developed a highly selective and stable catalyst CoSe2 nanoparticle hybridized with carbon nanotubes (CoSe2@CNTs). The CoSe2@CNTs hybrid catalysts performed an extraordinary high selectivity for NH4 + formation in NO electroreduction with minimal N2O production and H2 evolution. The specific spatial structure of CoSe2 is conductive to the predominant formation of N-H bond between the N from adsorbed NO and H and inhibition of N-N formation from adjacent adsorbed NO. It was also the first time to convert the coordinated NO into NH4 + using non-noble metal catalysis. Moreover, the original concept of employing CoSe2 as eletrocatalyst for NO hydrogenation presented in this work can broaden horizons and provide new dimensions in the design of new highly efficient catalysts for NH4 + synthesis in aqueous solution.

  相似文献   
10.
热解温度和时间对污泥生物碳理化性质的影响   总被引:2,自引:0,他引:2  
污泥热解制备生物碳是一种环境友好的污泥处理处置途径。重点考察了热解温度及时间等因素对生物碳品质的影响。污泥取自厦门某城市污水处理厂脱水污泥(初始含水率为80%),热解实验结果表明,随着热解温度的升高(从300~700℃),热解时间的增加(2~4 h),生物碳产率均下降;低温热解时(300℃),生物碳偏酸性,而高温热解时(700℃),生物碳偏碱性;生物碳N含量随着热解温度的升高、热解时间的增加而降低,而P、K及微量元素随着热解温度的升高,热解时间的增加而增加。DTPA浸提实验结果表明,高温热解能降低污泥生物碳中微量元素的有效性。  相似文献   
设为首页 | 免责声明 | 关于勤云 | 加入收藏

Copyright©北京勤云科技发展有限公司  京ICP备09084417号