载银TiO2半导体催化剂降解染料水溶液的研究

以新型载银ＴｉＯ２为催化剂,采用高压汞灯为光源对染料水溶液进行光催化降解。实验结果表明：采用ＴｉＯ２催化剂使直接耐酸大红（３５ｍｇ／Ｌ）、直接耐晒翠蓝（５０ｍｇ／Ｌ）和直接黑（５０ｍｇ／Ｌ）染料溶液脱至无色的时间分别为３５ｍｉｎ、６０ｍｉｎ及６０ｍｉｎ,而采用载银ＴｉＯ２催化剂,上述染料溶液脱至无色的时间分别为２０ｍｉｎ、３０ｍｉｎ及２０ｍｉｎ。探讨了ｐＨ、光强、催化剂用量及灼烧温度等对催化降解的     

土壤理化条件变化对含硫气体释放的影响

研究在不同的室内培养条件下,土壤的各种物理化学条件对含硫气体释放的影响．结果表明,土壤在含水率为50%～75%,ｐＨ＝3.25～8.67,较大的Ｃ:Ｎ 条件下,各含硫气体的释放量较大．而光照条件对于不同的硫源释放含硫气体的情况各有不同．环境条件通过改变微生物的活动改变了各硫源的生化分解的产硫量     

无水条件下气相三氯乙烯的光催化降解研究

以二氧化钛为光催化剂,主波长254nm紫外线杀菌灯为光源,研究了气相三氯乙烯（TCE）在无水条件下的光催化降解反应。结果发现,TCE的光催化降解产物为HCl、CO₂及Cl₂,并得出TCE在无水条件下光催化反应的计量式为C₂HCl₃+2O2hv/TiO2→HCl＋2CO₂＋Cl₂,该计量式与有水条件下光催化反应降解TCE的计量式不同。结果还发现,TCE初始反应速率与光强的0.16次方呈正比,光催化降解速率方程符合Langmuir－Hinshelwood公式_〔1〕。     

半导体光催化降解分散染料溶液的研究

以ＴｉＯ２半导体为光催化剂对溶液中的分散染料的降解进行了研究，在通空气的条件下，光照５０分钟可使５０ｍｇ／Ｌ的染料溶液完全色，ＣＯＤ.ｒ作文经可达７０％以上。研究中探讨了通空气、溶液的ＰＨ值，光距ＴｉＯ２重复使用等因素对光催化降解的影响。     

水溶液中十二烷基苯磺酸钠的半导体光催化降解的研究

以ＴｉＯ２为催化剂,以３００Ｗ高压汞灯为光源,对水溶液中的十二烷基苯磺酸钠进行了半导体光催化降解,研究不同ｐＨ条件下金红石型和锐钛型ＴｉＯ２的光催化活性及Ｈ２Ｏ２,Ｃｕ＾２＋的加入对降解的影响,结果表明,锐钛型ＴｉＯ２具有较高的催化活性;Ｈ２Ｏ２在碱性条件下能抑制ＤＢＳ的光催化降解,在无ＴｉＯ２时,Ｈ２Ｏ２对ＤＢＳ有光催化氧化作用,在酸性条件下,Ｃｕ＾２＋对ＤＢＳ的ＴｉＯ２光催化降解有较强的助催化     

水溶液中α-萘乙酸的光降解研究

为了解α－萘乙酸在环境中滞留、迁移和转化等行为,以降低率紫外灯和荧光灯为光源,对水溶液中的ＮＡＡ进行光降解。研究结果表明,主波长为２５４ｎｍ的紫外光能有效降解ＮＡＡ,降解呈一级动力学反应,而主波长为３６５ｎｍ的长波光对ＮＡＡ几乎不降解;添加ＴｉＯ２能有效催化ＮＡＡ的降解,采用ＧＣ－ＭＳ技术鉴定了几种光解主要产物,ＮＡＡ的光降解包括氧化脱羧和芳环的氧化断裂过程。     

Degradation of tris(1-chloro-2-propanyl) phosphate by the synergistic effect of persulfate and zero-valent iron during a mechanochemical process

This study revealed a dual pathway for the degradation of tris(1-chloro-2-propanyl) phosphate (TCPP) by zero-valent iron (ZVI) and persulfate as co-milling agents in a mechanochemical (MC) process. Persulfate was activated with ZVI to degrade TCPP in a planetary ball mill. After milling for 2 h, 96.5% of the TCPP was degraded with the release of 63.16, 50.39, and 42.01% of the Cl^?, SO₄^2?, and PO₄^3?, respectively. In the first degradation pathway, persulfate was activated with ZVI to produce hydroxyl (·OH) radicals, and ZVI is oxidized to Fe(II) and Fe(III). A substitution reaction occurred as a result of the attack of ·OH on the P–O–C bonds, leading to the successive breakage of the three P–O–C bonds in TCPP to produce PO₄^3?. In the second pathway, a C–Cl bond in part of the TCPP molecule was oxidized by SO₄·^? to carbonyl and carboxyl groups. The P–O–C bonds continued to react with ·OH to produce PO₄^3?. Finally, the intermediate organochloride products were further reductively dechlorinated by ZVI. However, the synergistic effect of the oxidation (·OH and SO₄·^?) and the reduction reaction (ZVI) did not completely degrade TCPP to CO₂, resulting in a low mineralization rate (35.87%). Moreover, the intermediate products still showed the toxicities in LD₅₀ and developmental toxicant. In addition, the method was applied for the degradation of TCPP in soil, and high degradations (>?83.83%) were achieved in different types of soils.