基于厌氧氨氧化和中温亚硝化的可持续生物脱氮工艺

通过介绍厌氧氨氧化技术（ANAMMOX）和亚硝化技术（SHARON）在污水脱氯处理中的原理,着重从工艺特性分析以及控制因数方面介绍SHARON—ANAMMOX联合工艺,并通过与传统工艺的比较,指出SHARON—ANAMMOX联合工艺是可持续性处理工艺。     

三维电极法处理苯酚废水影响因素研究

根据电解原理,采用自制三维电极反应器对苯酚废水进行处理。在pH值为3,反应时间为120min,电解电压为15V,极板间距为10cm,曝气强度为0.6m3/h反应条件下,苯酚和COD的最大去除率分别为89.1%和83.2%。表明三维电极法适用于处理浓度较高、且有毒性的废水,是快捷、经济、高效的废水处理方法。     

影响三沟式氧化沟脱氮效果的2个重要参数

运行周期中反硝化运行和硝化运行的时间比ｔＤＮ／ｔＮ是平衡处理系统反硝化,硝化能力的重要参数,实验室条件下分别比较了ｔＤＮ／ｔＮ为０．２７,０．４０,０．４７,０．７５和１．０的５种不同组合的运行效果。结果表明,当ｔＤＮ／ｔＮ为０．４０时,即硝化能力略大于反硝化潜能时,脱氮效果最好。     

含硫油品储罐自燃着火原因的研究

简述了储罐中硫化亚铁形成的过程和硫化亚铁引发储罐自燃的机理,并模拟储罐中硫化亚铁的形成过程,对其进行氧化实验,证明储罐腐蚀产物一硫化亚铁氧化放热是引发储罐着火的原因之一。     

碳纳米管催化电极处理难降解有机物研究进展

难降解有机物严重污染环境和威胁人类身体健康,因此难降解有机物的治理技术研究是目前水污染防治研究的热点与难点。碳纳米管(CNTs)由于具有独特的一维结构、良好的化学稳定性、优异的电荷传导性能以及独特的电学性能,近些年被广泛应用做电极材料。介绍了碳纳米管的电化学特性,对碳纳米管催化电极的制备、催化反应机理及其在有机污染物处理过程中的应用进行了概述,并对其应用前景进行了展望。     

Experimental investigation into the oxidation reactivity, morphology and graphitization of soot particles from diesel/n-octanol mixtures

Aiming to investigate the impacts of n-octanol addition on the oxidation reactivity, morphology and graphitization of diesel exhaust particles, soot samples were collected from a four-cylinder turbocharged diesel engine fueled with D100（neat diesel fuel）, DO15（85% diesel and 15% n-octanol, V/V） and DO30（70% diesel and 30% n-octanol, V/V）. All tests were conducted at two engine speeds of 1370 and 2150 r/min under a fixed torque of 125 N ·m. The soot properties were characterized by thermogravimet...     

Degradation of bisphenol A by photo-fenton processes

The photo-Fenton reactions, which could yield hydroxyl radicals via the catalytic degradation of H₂O₂ by Fe(II), were focused as one of the abiotic degradation processes of bisphenol A (BPA) in surface waters. At pH 6, in the presence of H₂O₂ only, 32% of BPA was degraded after 120?min of irradiation. However, 97% of BPA was degraded in the presence of both H₂O₂ and Fe(II). Without light irradiation, no BPA degradation was observed even in the presence of Fe(II) and H₂O₂. These results show that photo-Fenton processes are effective in the natural attenuation of BPA in surface water. In addition, the presence of humic acids (HAs), which were of more aliphatic nature, resulted in enhancing BPA degradation via the photo-Fenton processes. Therefore, HAs can be one of the important factors in enhancing the degradation of BPA in surface water via the photo-Fenton processes.     

臭氧-生物活性炭技术在微污染饮用水处理中的应用

通过研究国内外臭氧—生物活性炭工艺的发展现状和应用实践，指出了该项技术在应用中体现出的优越性，并提出了此项技术在应用中存在的问题，部分地介绍了提高此项技术应用水平的措施。研究表明，臭氧—生物活性炭工艺在处理微污染饮用水将会受到重视和广泛地推广应用，同时也对今后的研究方向提出了相应的观点。     

Product identification and toxicity change during oxidation of methotrexate by ferrate and permanganate in water

• Oxidation of methotrexate by high-valent metal-oxo species was first explored. • Fe(VI) presented a higher reactivity to MTX than Mn(VII) at pH 8.0. • Ketonization and cleavage of peptide bond were two initial reaction pathways. • Products of MTX were not genotoxic, neurotoxic, or endocrine-disrupting chemicals. • The less biodegradable products exhibited developmental and acute/chronic toxicity. Accompanying an annual increase in cancer incidence, the global use of anticancer drugs has remarkably increased with their worldwide environmental prevalence and ecological risks. In this study, the oxidation of methotrexate (MTX), a typical anticancer drug with ubiquitous occurrence and multi-endpoint toxicity, by ferrate(VI) (Fe(VI)) and permanganate (Mn(VII))) was investigated in water. Fe(VI) exhibited a higher reactivity with MTX (93.34 M⁻¹ s⁻¹) than Mn(VII) (3.01 M⁻¹ s⁻¹) at pH 8.0. The introduction of Cu(II) and Fe(III) at 1.0 mM improved the removal efficiency of 5.0 μM MTX by 100.0 μM Fe(VI) from 80% to 95% and 100% after 4 min, respectively. Seven oxidized products (OPs) were identified during oxidative treatments, while OP-191 and OP-205 were characterized as specific products for Fe(VI) oxidation. Initial ketonization of the L-glutamic acid moiety and cleavage of the peptide bond of MTX were proposed. Additionally, a multi-endpoint toxicity evaluation indicated no genotoxicity, neurotoxicity, or endocrine-disrupting effects of MTX and its OPs. Particularly, serious developmental toxicity in zebrafish larvae was observed in the treated MTX solutions. Based on the acute and chronic aquatic toxicity prediction, OP-190, OP-192, OP-206, and OP-208 were deemed toxic or very toxic compared to harmful MTX. Furthermore, the reduced biodegradability index from 0.15 (MTX) to −0.5 to −0.2 (OP-192, OP-206, and OP-468) indicated the formation of lower biodegradable OPs. Overall, this study suggests that Fe(VI) and Mn(VII) oxidation are promising treatments for remediating anticancer drug-contaminated water. However, the environmental risks associated with these treatments should be considered in the evaluation of water safety.     

Chromium transport, oxidation, and adsorption in manganese-coated sand

We examine how the processes of advection, dispersion, oxidation-reduction, and adsorption combine to affect the transport of chromium through columns packed with pyrolusite (beta-MnO2)-coated sand. We find that beta-MnO2 effectively oxidizes Cr(III) to Cr(VI) and that the extent of oxidation is sensitive to changes in pH, pore water velocity, and influent concentrations of Cr(III). Cr(III) oxidation rates, although initially high, decline well before the supply of beta-MnO2 is depleted, suggesting that a reaction product inhibits the conversion of Cr(III) to Cr(VI). Rate-limited reactions govern the weak adsorption of each chromium species, with Cr(III) adsorption varying directly with pH and Cr(VI) adsorption varying inversely with pH. The breakthrough data on chromium transport can be matched closely by calculations of a simple model that accounts for (1) advective-dispersive transport of Cr(III), Cr(VI), and dissolved oxygen, (2) first-order kinetics adsorption of the reduced and oxidized chromium species, and (3) nonlinear rate-limited oxidation of Cr(III) to Cr(VI). Our work supplements the limited database on the transport of redox-sensitive metals in porous media and provides a means for quantifying the coupled processes that contribute to this transport.