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31.
硫酸渣制备高纯度硫酸亚铁   总被引:1,自引:0,他引:1  
以高铁硫酸渣为原料,采用酸浸一还原-除杂-结晶-重结晶-干燥工艺,合成高纯度硫酸亚铁.通过反应温度、反应时闻对硫酸渣中铁的浸出率的影响,以及结晶温度、干燥温度,干燥时间、于燥时间对硫酸亚铁产品纯度的影响做分析实验,得出最佳酸浸条件:硫酸渣与硫酸的固液比为1:3,硫酸质量分数为20%-25%,反应温度为80℃,反应时间为6 h,搅拌强度为200 r/min;最佳结晶精制条件:结晶溶液pH值1:3,温度为60℃,温度海60℃;除杂最佳条件:pH值约为4.5;冷却结晶温度控制在20℃,结晶秣过程为30℃于燥6 h.  相似文献   
32.
发展循环经济 开辟航空业新纪元   总被引:1,自引:0,他引:1  
随着人们环保意识的逐渐增强,航空业所造成的环境和噪声污染已经越来越成为令人关注的重大问题.从5个方面介绍了发达国家航空业发展循环经济的经验,指出我国作为发展中国家,要正视与发达国家的差距,借鉴国外先进经验,转变观念、大胆创新,大力发展循环经济,开辟我国航空业的新纪元.  相似文献   
33.
利用IED22000A便携式微机多道能谱仪对成都市区土壤的天然放射性核素进行了直接就地测量,估算出天然环境放射性核素^238U、^232Th、^40K的比活度范围分别为10.37~77.19Bq/kg、17,85~225.74Bq/kg、284.83~892.67Bq/kg;外照射指数范围为0.16—0.8;离地面1m高的空气吸收剂量率均值为83.23nGy/h;1外照射年有效剂量当量为0.34~0.70mSv;等效镭浓度的变化范围是59.06-386.45Bq/kg,均值为164.15Bq/kg。各项指标均在容许范围之内,因而成都市属于外照射水平的安全区域,人居环境不受影响。  相似文献   
34.
通过对民营企业北京蟹岛集团的实地调查,对其以“低消耗、低排放、低污染、高效益”为经营方针,以“生态、环保、可持续”为经营理念,成功实现“资源-消费-再利用”的循环经济增长模式进行详细介绍。并通过蟹岛集团自身的发展证明:循环经济不仅可以改变传统“资源-效益—废弃物”的线性增长模式,还可以促进企业的发展,为企业带来可观的经济效益。  相似文献   
35.
36.
This study aimed to determine the occurrence, abundance, and fate of nine important antimicrobial resistance genes (ARGs) (sul1, sul2, tetB, tetM, ermB, ermF, fexA, cfr, and Intl1) in the simulated soil and pond microcosms following poultry and swine manure application. Absolute quantitative PCR method was used to determine the gene copies. The results were modeled as a logarithmic regression (N?=?mlnt?+?b) to explore the fate of target genes. Genes sul1, Intl1, sul2, and tetM had the highest abundance following the application of the two manure types. The logarithmic regression model fitted the results well (R 2 values up to 0.99). The reduction rate of all genes (except for the genes fexA and cfr) in manure-pond microcosms was faster than those in manure-soil microcosms. Importantly, sul1, intl1, sul2, and tetM had the lowest reduction rates in all the samples and the low reduction rates of tetM was the first time to be reported. These results indicated that ARG management should focus on using technologies for the ARG elimination before the manure applications rather than waiting for subsequent attenuation in soil or water, particularly the ARGs (such as sul1, intl1, sul2, and tetM investigated in this study) that had high abundance and low reduction rate in the soil and water after application of manure.  相似文献   
37.
Sun  Zhigao  Li  Jiabing  He  Tao  Ren  Peng  Zhu  He  Gao  Hui  Tian  Liping  Hu  Xingyun 《Environmental science and pollution research international》2017,24(29):23080-23095
Environmental Science and Pollution Research - Sediment samples were collected in five marshes (C1, Phragmites australis marsh; C2, P. australis and Cyperus malaccensis marsh; C3, C. malaccensis...  相似文献   
38.

In order to remove arsenic (As) from contaminated water, granular Mn-oxide-doped Al oxide (GMAO) was fabricated using the compression method with the addition of organic binder. The analysis results of XRD, SEM, and BET indicated that GMAO was microporous with a large specific surface area of 54.26 m2/g, and it was formed through the aggregation of massive Al/Mn oxide nanoparticles with an amorphous pattern. EDX, mapping, FTIR, and XPS results showed the uniform distribution of Al/Mn elements and numerous hydroxyl groups on the adsorbent surface. Compression tests indicated a satisfactory mechanical strength of GMAO. Batch adsorption results showed that As(V) adsorption achieved equilibrium faster than As(III), whereas the maximum adsorption capacity of As(III) estimated from the Langmuir isotherm at 25 °C (48.52 mg/g) was greater than that of As(V) (37.94 mg/g). The As removal efficiency could be maintained in a wide pH range of 3~8. The presence of phosphate posed a significant adverse effect on As adsorption due to the competition mechanisms. In contrast, Ca2+ and Mg2+ could favor As adsorption via cation-bridge involvement. A regeneration method was developed by using sodium hydroxide solution for As elution from saturated adsorbents, which permitted GMAO to keep over 75% of its As adsorption capacity even after five adsorption–regeneration cycles. Column experiments showed that the breakthrough volumes for the treatment of As(III)-spiked and As(V)-spiked water (As concentration = 100 μg/L) were 2224 and 1952, respectively. Overall, GMAO is a potential adsorbent for effectively removing As from As-contaminated groundwater in filter application.

  相似文献   
39.
Sun J  Hu J  Peng H  Shi J  Dong Z 《Chemosphere》2012,87(1):37-42
Increasing antibacterial resistance and pathogenicity in the environment is of growing concern due to its potential human risk. In the present study, 236 Escherichia coli isolates were collected from Wenyu River in China on drugless (48 isolates) and quinolone-containing plates (189 isolates). Their minimum inhibitory concentrations (MICs) were determined ranging from 0.125 μg mL−1 to 128 μg mL−1. Mutation points related to fluoroquinolone resistance were observed at S83 to L and D87 to N or Y in the GyrA subunit and S80 to R or I and E84 to G in the ParC subunit. Generally, MICs of LEV and GAT are dependent on the patterns of these mutation points. The profile with three mutation points was related to LEV-resistant E. coli isolates, and the (S83L, D87N + S80I) mutation profile was most prevalent (65.7%) in LEV-resistant isolates, while a large proportion of isolates, even those with three mutation points, were susceptive to GAT. The incidence of virulence factors in LEV-resistant isolates (44.7%, 59/132) was much higher than in nonresistant isolates (23.1%, 24/104) (χ2 = 11.925, 1° of freedom, p < 0.001) indicating that fluoroquinolone-resistant E. coli would pose a potential risk. A similar distribution was also found in isolates resistant to GAT (χ2 = 7.843, 1° of freedom, = 0.0079).  相似文献   
40.
This article investigates the effects of stone powder sludge on the microstructure and strength development of alkali-activated fly ash and blast furnace slag mixes. Stone powder sludge produced from a crushed aggregate factory was used to replace fly ash and granulated blast furnace slag at replacement ratios of 0%, 10%, 20%, and 30% by mass. The unit weight and compressive strength of the samples were measured, and scanning electron microscopy/energy dispersive spectroscopy and X-ray diffraction (XRD) analyses were performed. The test results indicated that the compressive strength of alkali-activated blast furnace slag mixes using stone powder sludge was higher than that of the alkali-activated blast furnace slag control mix, but the compressive strength of alkali-activated fly ash mixes decreased with increasing replacement ratio of stone powder sludge. Microscopy results indicated that for alkaliactivated blast furnace slag samples, broken surfaces were more evident than for the alkali-activated fly ash samples. For all XRD diagrams, broad and diffuse peaks were observed around 2θ = 35° (d = 2.96–3.03 Å), implying amorphous or short-ordering structure phases.  相似文献   
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