纳米零价铁和零价铁对餐厨垃圾暗发酵制氢过程铁离子和酶活性的影响

通过投加不同浓度的纳米零价铁(NZVI)和零价铁(ZVI),考察了暗发酵制氢过程中铁离子组成和浓度变化、氢化酶和脱氢酶活性,研究了2种添加剂强化餐厨垃圾高温((55±1) ℃)暗发酵制氢的作用机制。结果表明：投加NZVI和ZVI均可提高餐厨垃圾暗发酵制氢性能;当投加100 mg·L⁻¹ ZVI时,产氢效果最佳,最大产氢潜力和最大产氢速率分别为425.72 mL和66.32 mL·h⁻¹,是投加NZVI实验组的1.64倍和1.34倍,代谢途径是以乙醇型发酵为主的混合型发酵;在投加NZVI和ZVI后,暗发酵制氢末端产物的Fe²⁺和Fe³⁺浓度升高,投加300 mg·L⁻¹ NZVI和100 mg·L⁻¹ ZVI实验组Fe²⁺浓度最大,是未投加实验组的2倍和1.87倍;与反应前相比,Fe²⁺显著升高,Fe³⁺由于微生物利用与转化浓度降低,同时可有效提高氢化酶活性。投加100 mg·L⁻¹ ZVI不仅可提高氢化酶活性,还可提高脱氢酶活性。以上结果可为提高餐厨垃圾等复杂有机废物的高效能源化提供参考。     

硫酸盐还原菌污泥固定化特性

采用玉米芯为碳源,聚乙烯醇(PVA)为包埋载体,饱和硼酸(H3BO3)为交联剂,研究了硫酸盐还原菌污泥(SRBS)、铁屑、麦饭石共固处理合成煤矿酸性废水的最优配比与机理,并分析了固定化过程中小球稳定性及活性的变化规律。实验结果表明,SRBS投加量是影响处理效果的最显著因子,当投加30%SRBS、2%铁屑、3%麦饭石时SO42-、Mn2+去除率分别为94.13%和84.39%,溶液pH为7.03,未检测出Fe2+;随着交联时间的延长,小球膨胀率及SO42-还原率分别呈线性与指数下降,从保持小球稳定性与活性角度考虑,可将交联时间设定为4~8 h;该法可为市政污泥的处置以及生物法处理煤矿酸性废水的工程应用提供技术参考。     

超声波-铁粉协同降解五氯酚

通过超声波-铁粉联合体系协同降解废水中的五氯酚(PCP).实验结果表明:降解120 min后,PCP去除率可达90.4％;在该体系中铁粉被逐渐腐蚀成Fe2+,随降解时间的延长,Fe2+浓度逐渐增加;体系中的Fe2+可以促进·OH的产生,并且可以与超声空化作用下产生的H2O2发生Fenton试剂氧化反应降解PCP;超声波...     

THE IMPACT OF URBANIZATION ON THE DISTRIBUTION OF HEAVY METALS IN BOTTOM SEDIMENTS OF THE SADDLE RIVER1

ABSTRACT: A three-year study has been conducted on a 4.6 mile stretch of the Saddle River near Lodi, New Jersey. The primary objectives of this investigation were (1) to provide baseline information on the concentration and distribution of heavy metals in bottom sediments of the Saddle River; (2) to qualitatively evaluate which parameters affect this distribution; and (3) to determine the effect of urbanization on the concentration and distribution of these materials. Significant enrichments of several heavy metals were observed in bottom sediments of the lower Saddle River near Lodi, New Jersey, as compared to the upper Saddle River. Attempts to correlate metal concentrations in bottom sediments with chemical-oxygen demand were not successful in demonstrating a relationship between these two factors. Metal concentrations were found to be strongly dependent upon particle size. In general, metal concentrations in bottom sediments increased with decreasing partical diameter. However, metals enrichment was observed to be considerably greater in the larger sediment fractions studied (>420μ) than the smaller sediment fractions as one proceeded downstream through the urban area. Since the larger sediment fractions are least effected by scour and transport they may best reflect the effect of urbanization on the distribution of heavy metals over an extended period of time at a given location.     

木屑对铁尾矿磁化焙烧磁选工艺的影响

由于我国铁尾矿堆存量大、铁品位低,导致其资源化利用率低,因此,以木屑生物质作还原剂回收铁尾矿中的铁元素,考察不同焙烧温度、焙烧时间、木屑添加量等对铁尾矿磁化焙烧的影响。结果表明：木屑磁化焙烧提高铁尾矿磁性性能的最佳焙烧条件为焙烧温度750 ℃、木屑添加量15%及焙烧时间40 min;在该条件下,铁精矿品位为62.84%,且铁回收率为94.58%。经物相分析发现,原铁尾矿中,含铁矿物主要为赤铁矿,而焙烧后主要以磁铁矿为主。振动样品磁强计分析表明,铁矿石的饱和磁化强度从0.04 emu·g⁻¹提高到了46.01 emu·g⁻¹。以木屑生物质作为还原剂进行铁尾矿磁化焙烧,可较好地提高其中铁的品位和磁化强度,从而实现铁矿石的低强度磁选分离。     

基于煤矸石制备的聚合氯化铝铁钛及其在二沉池出水处理中的应用

以煤矸石酸浸液为原料,经过钛掺杂、聚合、熟化和浓缩干燥等过程,制备了高效无机高分子混凝剂聚合氯化铝铁钛(PTAFC)。分别考察了钛投加量、pH、聚合温度、聚合时间对PTAFC混凝性能的影响,同时研究了PTAFC对城镇污水处理厂二沉池出水浊度、COD、总磷和氨氮的去除效果,并与聚合氯化铝铁(PAFC)进行了对比。结果表明：在钛铁摩尔比0.3、pH=1.5、聚合温度60 ℃、聚合时间3 h、常温熟化24 h时,所制得的PTAFC性能最佳;在投加量70 mg·L⁻¹、pH=7、反应温度20 ℃、慢速搅拌速度40 r·min⁻¹的混凝条件下,对自配水的浊度、COD和UV₂₅₄的去除效果最好,去除率分别为99.13%、37.25%和39.9%。PTAFC对城镇污水处理厂二沉池出水的浊度和总磷有极好的去除效果,同时对COD和氨氮有一定去除能力,污染物去除能力明显优于PAFC。上述研究成果对有效减少煤矸石的堆存量、拓宽煤矸石利用渠道,实现混凝剂的低成本、高效率工业化生产和应用具有重要的意义。     

氧化铁改性砂联合生物预处理对氨氮的吸附特性

对含氨氮(NH3-N)的微污染原水,采用自制氧化铁改性石英砂(iron oxide coated sand,IOCS)滤料强化过滤与生物预处理技术联合,进行强化处理与吸附效果研究.结果表明,采用强化挂膜法,生物预处理反应器的生物膜成熟期约为7 d,其对氨氮的去除率为60%~70%,但反应器中存在亚硝酸盐氮积累的现象.IOCS与生物预处理技术联合,对NH3-N的平均去除率为84.67%,出水NH3-N浓度均低于0.5 mg/L,NO2--N含量趋于0;而普通石英砂(RQS)在同等条件下,对氨氮的去除效果不稳定,平均去除率为74.31%,出水NH3-N平均浓度未达标,对NO2--N平均去除率仅有33.29%.在4 m/h滤速工况下,与生物预处理技术联合,IOCS和RQS对NH3-N最高去除率分别为94.3%和82.72%.IOCS与RQS的表面形态结构存在明显差异:前者的表面结构更加复杂多孔,比表面积大,有利于生物牢固附着;后者表面较光滑,比表面积小,挂膜后生物易脱落.     

Pah characteristics in ambient air within a steel industrial complex

Ambient air samples at ten sites in an iron and steel industrial complex were collected from June to December for analyzing polycyclic aromatic hydrocarbons (PAHs). Sixteen species of PAH components in air samples were identified. The results indicate that both gaseous phase and particle‐bound PAHs at the top of the cokemaking plants are unusually high. The profiles of particle‐bound PAHs indicate that the predominant species at the top of, the coke oven batteries are those of high molecular weight components. The major components of particle‐bound PAHs at sampling sites near the fenceline, however, include the medium molecular weight components. The PAH profiles of air samples within the industrial complex show a strong similarity to those of cokemaking plant samples. The concentrations and the specific content of benzo(a)pyrene in the iron and steel industrial complex are higher than those values measured in urban area, petrochemical industry park, and open‐air burning area.     

纳米零价铁对溶液中PCB77的降解及其影响因素

设计了以溶液初始pH值、3,3’,4,4’-四氯联苯(PCB77)初始浓度、纳米零价铁(Fe0)投加量、纳米零价硅(Si0)投加量、腐殖酸和环糊精浓度为影响因素的正交试验,研究纳米Fe0降解PCB77时各因素对反应体系中PCB77残留率、氢离子浓度及氧化还原电位变化的影响及其相互关系。结果表明,在溶液初始pH值为4.5,初始ρ(PCB77)为1 mg.L-1,纳米Fe0投加量为10 g.L-1,纳米Si0投加量为0,ρ(腐殖酸)为0.25 g.L-1,ρ(环糊精)为1 g.L-1时,反应2 h后,PCB77残留率最低,为35.2%。溶液初始pH值对反应体系中PCB77的残留率影响最大,纳米Fe0投加量次之;溶液初始pH值对反应体系中氢离子浓度变化影响最大,环糊精投加量次之;PCB77初始浓度对反应体系中氧化还原电位变化影响最大,纳米Fe0投加量次之。     

Performance and mechanism of Cr(VI) removal by zero-valent iron loaded onto expanded graphite

Zero-valent iron (ZVI) was loaded on expanded graphite (EG) to produce a composite material (EG-ZVI) for efficient removal of hexavalent chromium (Cr(VI)). EG and EG-ZVI were characterized by X-ray diffraction (XRD), scanning electron microscopy (SEM), Fourier-transform infrared (FTIR) spectroscopy and Brunauer–Emmett–Teller (BET) analysis. EG-ZVI had a high specific surface area and contained sub-micron sized particles of zero-valent iron. Batch experiments were employed to evaluate the Cr(VI) removal performance. The results showed that the Cr(VI) removal rate was 98.80% for EG-ZVI, which was higher than that for both EG (10.00%) and ZVI (29.80%). Furthermore, the removal rate of Cr(VI) by EG-ZVI showed little dependence on solution pH within a pH range of 1–9. Even at pH 11, a Cr(VI) removal rate of 62.44% was obtained after reaction for 1 hr. EG-ZVI could enhance the removal of Cr(VI) via chemical reduction and physical adsorption, respectively. X-ray photoelectron spectroscopy (XPS) was used to analyze the mechanisms of Cr(VI) removal, which indicated that the ZVI loaded on the surface was oxidized, and the removed Cr(VI) was immobilized via the formation of Cr(III) hydroxide and Cr(III)–Fe(III) hydroxide/oxyhydroxide on the surface of EG-ZVI.