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61.
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
62.
Xuemin Hao Guanlong Wang Shuo Chen Hongtao Yu Xie Quan 《Frontiers of Environmental Science & Engineering》2019,13(5):77
63.
采用溶胶-凝胶法,在聚苯乙烯(PS)/CdS核壳纳米颗粒表面包覆致密TiO_2层,制备出具有双壳层结构的PS/CdS/TiO_2纳米复合颗粒,考察了制备条件对材料结构的影响,并利用甲基橙溶液对其光催化性能进行了评价。SEM、TEM、XRD和FTIR分析结果表明,制得的微球单分散性良好,壳层包覆完整,厚度均匀。PS/CdS/TiO_2制备的适宜反应时间为12~18 h,适宜反应pH为7~9。PS/CdS/TiO_2较PS/CdS具有更为优异的可见光催化性能。 相似文献
64.
采用共沉淀法合成了不同Ce与Ti摩尔比的CePO4-TiO2复合材料,利用XRD、TEM、NH3-TPD和H2-TPR技术对其物理化学性质进行了表征,并对其NH3-SCR活性进行了评价。实验结果表明:随着CePO4含量的增加,催化剂的活性提高;当Ce与Ti的摩尔比为8:2时催化剂的活性最高,230 ℃的NO转化率达到100%,且具有更广的温度窗口,优于纯CePO4。表征结果显示,CePO4与TiO2形成固溶体后,颗粒尺寸较为均匀,强酸位的数量增多,氧化还原性能提升,从而提高了催化剂的SCR反应活性,同时改善了其抗水抗硫性能。 相似文献
65.
66.
67.
吸附模式对有机物光催化降解的影响2.H-酸在TiO2表面的光催化降解途径 总被引:2,自引:1,他引:2
水溶液中H-酸通过磺酸基团吸附在TiO2表面,UV照射TiO2所产生的自由基首先进攻吸附在TiO2表面的磺酸基团,从而进一步导致萘环开环.pH 2.5条件下,虽然饱和吸附量较大,但由于H-酸仅通过一个磺酸基团吸附在TiO2表面,过程中产生的硫酸根速率较慢,最终的光降解速率也较慢.pH 5.0条件下,虽然饱和吸附量较小,但由于吸附在TiO2表面的两个磺酸基团同时受到来自TiO2表面自由基的进攻,过程中产生的硫酸根速率较快,最终的光降解速率也较快.吸附模式的差异是导致H-酸在不同pH值条件下光催化降解途径和速率差异的关键因素. 相似文献
68.
69.
70.
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