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71.
Introduction Aromatic sulfonic acid, which is produced in large amounts in chemical industry since the end of 19th century, has been widely applied in many industrial processes, including the various steps of procedure (Alonso and Barcelo, 2000). Naphthalene- sulfonic acids are of importance as dye intermediates and commonly used in the textile auxiliary industry employing many azo dyes and pigments. Among them, 1-naphthol-5-sulphonic acid (L-acid) is widely used in the printing as the raw ma… 相似文献
72.
Background, Aim and Scope
Due to their large potential for manifold applications, the use of nanoparticles is of increasing importance. As large amounts
of nanoparticles may reach the environment voluntarily or by accident, attention should be paid on the potential impacts on
the environment. First studies on potential environmental effects of photocatalytic TiO2 nanoparticles have been performed
on the basis of widely accepted, standardized test systems which originally had been developed for the characterization of
chemicals. The methods were adapted to the special requirements of testing photocatalytic nanoparticles.
Materials and Methods:
Suspensions of two different nanoparticles were illuminated to induce their photocatalytic activity. For testing, the growth
inhibition test with the green alga Desmodesmus subspicatus and the immobilization test with the daphnid Daphnia magna were
selected and performed following the relevant guidelines (algae: ISO 8692, OECD 201, DIN 38412-33; daphnids: ISO 6341, OECD
202, DIN 38412-30). The guidelines were adapted to meet the special requirements for testing photocatalytic nanoparticles.
Results:
The results indicate that it is principally possible to determine the ecotoxicity of nanoparticles. It was shown that nanoparticles
may have ecotoxicological effects which depend on the nature of the particles. Both products tested differ in their toxicity.
Product 1 shows a clear concentration-effect curve in the test with algae (EC50: 44 mg/L). It could be proven that the observed
toxicity was not caused by accompanying contaminants, since the toxic effect was comparable for the cleaned and the commercially
available product. For product 2, no toxic effects were determined (maximum concentration: 50 mg/L). In the tests with daphnids,
toxicity was observed for both products, although the concentration effect-curves were less pronounced. The two products differed
in their toxicity; moreover, there was a difference in the toxicity of illuminated and non-illuminated products.
Discussion:
Both products differ in size and crystalline form, so that these parameters are assumed to contribute to the different toxicities.
The concentration-effect curves for daphnids, which are less-pronounced than the curves obtained for algae, may be due to
the different test organisms and/or the differing test designs. The increased toxicity of pre-illuminated particles in the
tests with daphnids demonstrates that the photocatalytic activity of nanoparticles lasts for a period of time.
Conclusions:
The following conclusions can be drawn from the test results: (I) It is principally possible to determine the ecotoxicity
of (photocatalytic) nanoparticles. Therefore, they can be assessed using methods comparable to the procedures applied for
assessing soluble chemicals. - (II) Nanoparticles may exert ecotoxicological effects, which depend on the specific nanoparticle.
- (III) Comparable to traditional chemicals, the ecotoxicity depends on the test organisms and their physiology. - (IV) The
photocatalytic activity of nanoparticles lasts for a relevant period of time. Therefore, pre-illumination may be sufficient
to detect a photocatalytic activity even by using test organisms which are not suitable for application in the pre-illumination-phase.
Recommendations and Perspectives:
First results are presented which indicate that the topic 'ecotoxicity and environmental effects of nanoparticles' should
not be neglected. In testing photocatalytic nanoparticles, there are still many topics that need clarification or improvement,
such as the cause for an observed toxicity, the improvement of the test design, the elaboration of a test battery and an assessment
strategy.
On the basis of optimized test systems, it will be possible to test nanoparticles systematically. If a potential risk by specific
photocatalytic particles is known, a risk-benefit analysis can be performed and, if required, risk reducing measures can be
taken. 相似文献
73.
74.
75.
分别研究了纳米TiO2 在主波长为 364nm的汞灯光照下催化氧化i C3H7OH和CH3COCH3水溶液的反应速率 .通过XRD ,TEM ,BET和FT IR PAS对催化剂进行表征 ,粉末的晶型主要为锐钛矿型 .平均粒径在 1 5nm左右 ,比表面积为 1 0 1 0± 0 2m2 ·g- 1 ,FT IR PAS的检测结果表明 ,CH3COCH3是i C3H7OH光催化氧化的中间产物 ,其光催化氧化反应为 :i C3H7OH [O]CH3COCH3[O]CH3COOH[O]…[O]CO2 H2 O 相似文献
76.
Zr/TiO2纳米颗粒的制备及其光催化活性 总被引:1,自引:1,他引:1
以钛酸丁酯,乙醇为原料,用固相合成法制备了Zr/TiO2纳米颗粒,用XRD、TEM对其组成、颗粒大小、形貌进行了表征.通过对罗丹明B的降解反应,考察了Zr/TiO2的光催化活性.结果表明,Zr/TiO2为纳米颗粒,平均粒径为12.7 nm左右,且颗粒均匀;掺杂金属离子Zr提高了TiO2光催化效率,掺杂2.0%Zr的催化剂活性最高.Zr/TiO2的光催化反应,首先是反应物在Zr/TiO2表面发生吸附作用,然后进一步发生光催化降解. 相似文献
77.
负载型TiO2固定相光催化氧化法降解水中呋码唑酮 总被引:13,自引:0,他引:13
以高压汞灯为光源、负载在海砂上的TiO2为催化剂,采用敞口固定床型光催化反应器对水中难降解的呋码唑酮(FTD)进行了固定相光催化氧化实验。结果表明,反应速率可用LangmuirHinshelwood方程描述,与光分解相比,光催化氧化的突出优点是矿化程度高,相同光辐射条件下反应100min,0.10mmol/L的FTD水溶液经光催化氧化后TOC的去除率为89.1%,而经光分解后TOC的去除率仅为28.8%;在反应体系中投加少量臭氧或过氧化氢可以显著提高FTD的氧化效率,说明光催化氧化可以兼容O3/UV、H2O2/UV等光激发氧化工艺。制得的负载型TiO2具有较高的机械强度和化学稳定性,可重复利用。探讨了充氧、FTD浓度及pH值等对光催化氧化过程的影响。 相似文献
78.
以钛酸四丁酯为原料 ,膨胀珍珠岩为载体 ,用溶胶 -凝胶法制备可漂浮于水面的负载型TiO2 。利用该负载型TiO2 对罗丹明B(RB)进行光催化脱色实验 ,结果表明 ,浸渍 3次的负载型TiO2 光催化活性最高 ,催化剂最佳用量为 5 0 0mg/10 0mLRB ,经 5h光照 ,对 10 0mL浓度为 1mg/L和 2 .5mg/LRB脱色率分别为 76 .6 7%和 4 7.2 7% ;该催化剂使用寿命长 ,2 5h后催化剂脱色性能没有减弱 ,可重复使用 ;经 8h光照 ,染料废水脱色效果好。 相似文献
79.
附载型复合光催化剂TiO2·SiO2/beads降解有机磷农药 总被引:5,自引:0,他引:5
研究以四异丙醇钛 [Ti( iso- O C3 H7) 4]、硅酸乙酯为原料 ,以空心玻璃微球为载体 ,用溶胶—凝胶法制备可漂浮附载型复合光催化剂 Ti O2 · Si O2 / beads的过程 ,利用附载型复合光催化剂降解有机磷农药。结果表明 ,复合型光催化剂 Ti O2 · Si O2 摩尔比存在最佳值 ,n ( Ti O2 ) / m ( Si O2 ) =30 / 70时 ,光催化剂活性最高 ,其活性是同样降解条件下、同样含量 Degussa P- 2 5Ti O2 的 2倍左右。该光催化剂比表面大 ,吸附性强。并用 XRD和 SEM对附载型复合光催化剂进行表征 相似文献
80.