纳米铁酸镍的制备及可见光催化性能研究

利用水热法制备了纳米铁酸镍,表征了其微观结构和光谱性能,并以罗丹明B溶液作为目标污染物,研究了铁酸镍催化剂的可见光催化性能。结果表明:所制备铁酸镍的微观形貌为由直径200-300 nm左右的类似球形小颗粒组成的大颗粒,平均粒径为95.60 nm,在紫外-可见光谱区均有较强的光吸收。光催化过程中催化剂的适宜用量为0.05 g,少量H2O2的加入有助于提高罗丹明B溶液的降解率。催化剂用量为0.05 g,加入0.4 mL 30%的H2O2,降解50 mL 20 mg/L罗丹明B溶液,模拟太阳光照射240 min后降解率能够达到99.2%。在实际太阳光照射下,240 min后罗丹明B溶液的降解率可以达到85.2%。     

锰铈脱硝催化剂的制备及其再生性能研究

采用等体积浸渍法制备了一系列Mn-Ce-Ox复合氧化物脱硝催化剂用于NH3选择性催化还原(NH3-SCR)NO。考察了Mn/Ce摩尔比、焙烧温度、H2O和SO2对Mn-Ce-Ox复合氧化物脱硝催化剂活性的影响及催化剂中毒再生性能。结果表明:当NH3:NO=1:1,空速为5 000 h-1,550℃焙烧制得的Mn/Ce摩尔比为5∶1的Mn-Ce-Ox复合脱硝催化剂活性最佳,活性温度窗口为100~260℃,在此温度区间内催化剂活性大于90%。200℃时,Mn-Ce-Ox复合催化剂活性最高为97.84%;在10%(V/V)H2O蒸汽和300×10-6SO2共存条件下,200℃时,催化剂活性在开始反应2.5 h内迅速下降至53%左右,并在之后的6 h内没有明显变化;中毒催化剂经常温水洗再生处理、质量分数为3%的硝酸溶液再生处理和550℃焙烧2 h再生处理后200℃活性均能恢复到90%以上,其中中毒催化剂经质量分数为3%硝酸处理后活性恢复率最高。     

生物流化床短程硝化的快速启动及影响因素研究

采用内循环生物流化床反应器处理模拟高浓度氨氮废水,以确定其对处理高浓度氨氮废水的可行性,同时对试验条件进行了优化。结果研究表明:控制温度为(31±1)℃,利用反应器自身流化所携带溶解的空气,反应器内DO值可维持在1.5~2.5 mg/L,调节pH为8.0~8.5。经过42 d的污泥驯化适应时期,进水氨氮(NH4+-N)浓度由50 mg/L提高到300 mg/L。由于流化床采用填料载体微生物膜与活性污泥双重作用,同时载体呈流化状态,接触均匀,有巨大的比表面积,可以使床内保持高浓度的生物量,从而达到高效快速的传质效果。在HRT由开始的16 h缩短到8 h的条件下,氨氮(NH4+-N)的去除率达到90%以上,亚硝氮(NO2--N)的积累率达到75%。且在以后30 d的稳定运行阶段,氨氮(NH4+-N)去除率和亚硝氮(NO2--N)积累率均保持稳定。同时反应器最后出水水质澄清,无需二沉池及污泥处理。     

西安表土中多环芳烃的污染特征及其来源解析

通过2008年采集西安不同功能区表层土壤样品,运用GC/MS质谱联用仪对美国EPA优控的16种多环芳烃(PAHs)进行定性、定量分析,来探讨西安表层土壤种多环芳烃的污染特征及其来源。结果表明,16种PAHs均被检出,西安表土中ΣPAHs浓度范围为125~9 057 ng/g,平均值为2 727 ng/g,主要以4~6环PAHs为主,共占总量的69%。PAHs的空间分布规律为:工业区>文教区>绿化区>郊区>农村。应用特征比值判断法可知,西安表土中PAHs主要是煤的不完全燃烧和机动车尾气排放所产生的混合源污染。借鉴国外土壤污染标准可知西安城区表土污染较为严重。     

不同载体材料对厌氧氨氧化效果影响的研究

文章分别采用水性聚氨酯(WPU)和活性炭2种材料作为生物载体,在2个不同的上流式厌氧污泥床(UASB)反应器中接种包埋污泥和生物活性炭,采用人工配水进行连续实验,观测厌氧氨氧化反应器启动过程中各种含氮化合物的变化,以考察不同载体材料对厌氧氨氧化过程的影响。文章在生物活性炭反应器中成功驯化了采自污水处理厂的普通厌氧污泥,证明了从环境中驯化培养厌氧氨氧化菌的可能性。通过2个阶段中脱氮效率的比较,发现以水性聚氨酯包埋材料作为未驯化细菌载体并无明显优势,反而成为传质的障碍;而采用生物活性炭则可以迅速达到提高局部生物量、聚集功能菌、屏蔽不利环境的干扰等作用,是理想的微生物载体。     

生物滴滤塔处理制革恶臭气体微生物特性研究

在生物滴滤塔处理制革恶臭气体中,采用SBR法对活性污泥进行驯化,考查生物滴滤塔处理制革恶臭气体中微生物的特性。研究了微生物对氨氮和硫化物的去除效率以及驯化过程中污泥容积指数(SVI)的变化,并对挂膜后填料表面的微生物相进行扫描电镜观察。结果表明:经过19 d的驯化,微生物对氨氮和硫化物的去除率分别可以达到98.29%和94.16%,驯化期间污泥容积指数均保持在正常的范围之中。挂膜14 d的扫描电镜显示,填料表面有均匀的生物膜分布,说明微生物在填料上已经挂膜成功,驯化的微生物可以达到去除制革恶臭气体的要求。     

Fractionation of residual Al in natural water treatment from reservoir with poly-aluminum-silicate-chloride (PASiC): Effect of OH/Al, Si/Al molar ratios and initial pH

An aluminum fractionation study was conducted for a surface reservoir water treatment to understand the performance of poly-aluminum-silicate-chloride (PASiC) in terms of the residual Al fractions as a function of initial pH. The coagulation performance expressed as turbidity and organic matter removal was established as supporting data. Some extra data were evaluated in terms of the residual Al ratio of the composite PASiC coagulant. The main residual Al sources were the Al fractions derived from the use of PASiC. The turbidity and organic matter removal ability was optimal at initial pH 6.00-7.00, while the concentrations of various residual Al species and the residual Al ratio of PASiC were minimal at an initial pH range of 7.00-8.00. Under the conditions of OH/Al molar ratio = 2.00 and Si/Al molar ratio = 0.05, PASiC had superior coagulation performance and comparatively low residual Al concentrations. The Al fraction in the composite PASiC coagulant seldom remained under such conditions. Experimental data also indicated that the suspended (filterable) Al fraction was the dominant species, and organic-bound or organo-Al complex Al was considered to be the major species of dissolved Al in water treated by PASiC coagulation. Additionally, the dissolved inorganic monomeric Al species dominated the dissolved monomeric Al fraction.     

Nitrogen deposition alters soil chemical properties and bacterial communities in the Inner Mongolia grassland

Nitrogen deposition has dramatically altered biodiversity and ecosystem functioning on the earth; however, its effects on soil bacterial community and the underlying mechanisms of these effects have not been thoroughly examined. Changes in ecosystems caused by nitrogen deposition have traditionally been attributed to increased nitrogen content. In fact, nitrogen deposition not only leads to increased soil total N content, but also changes in the NH₄⁺-N content, NO₃^--N content and pH, as well as changes in the heterogeneity of the four indexes. The soil indexes for these four factors, their heterogeneity and even the plant community might be routes through which nitrogen deposition alters the bacterial community. Here, we describe a 6-year nitrogen addition experiment conducted in a typical steppe ecosystem to investigate the ecological mechanism by which nitrogen deposition alters bacterial abundance, diversity and composition. We found that various characteristics of the bacterial community were explained by different environmental factors. Nitrogen deposition decreased bacterial abundance that is positively related to soil pH value. In addition, nitrogen addition decreased bacterial diversity, which is negatively related to soil total N content and positively related to soil NO₃^--N heterogeneity. Finally, nitrogen addition altered bacterial composition that is significantly related to soil NH₄⁺-N content. Although nitrogen deposition significantly altered plant biomass, diversity and composition, these characteristics of plant community did not have a significant impact on processes of nitrogen deposition that led to alterations in bacterial abundance, diversity and composition. Therefore, more sensitive molecular technologies should be adopted to detect the subtle shifts of microbial community structure induced by the changes of plant community upon nitrogen deposition.     

Identification of rice cultivars with low brown rice mixed cadmium and lead contents and their interactions with the micronutrients iron, zinc, nickel and manganese

Paddy fields in mining areas are usually co-contaminated by a cocktail of mixed toxic heavy metals (e.g., Cd and Pb in Pb/Zn mines). However, previous studies on rice cultivars screened for effective metal exclusion have mostly focused on individual metals, and have been conducted under pot-trial or hydroponic solution conditions. This study identified rice cultivars with both low Cd and Pb accumulation under Cd-and Pb-contaminated field conditions, and the interactions of the toxic elements Cd and Pb with the micronutrient elements Fe, Zn, Mn and Ni were also studied. Among 32 rice cultivars tested, there were significant differences in Cd (0.06-0.59 mg/kg) and Pb (0.25-3.15 mg/kg) levels in their brown rice, and similar results were also found for the micronutrient elements. Significant decreases in concentrations of Fe and Mn were detected with increasing Cd concentrations and a significant elevation in Fe, Mn and Ni with increasing Pb concentrations. A similar result was also shown by Cd and Ni. Three cultivars were identified with a combination of low brown rice Cd and Pb, high micronutrient and grain yield (Wufengyou 2168, Tianyou 196 and Guinongzhan). Present results suggest that it is possible to breed rice cultivars with low mixed toxic element (Cd, Pb) and high micronutrient contents along with high grain yields, thus ensuring food safety and quality.     

活性污泥中超氧化物歧化酶(SOD)活性测定影响因素

研究以污水生物处理中的活性污泥为对象,采用氮蓝四唑光还原法测定超氧化物歧化酶(SOD)活性,从样品制备和保存方面探讨了是否添加溶菌酶液、细胞破碎时间、酶液保存时间与保存温度等因素对SOD活性测定的影响。研究表明,溶菌酶液的加入提高了细胞破碎效果;细胞破碎的条件为99次(工作3 s,停3 s),时间为40 min时破碎效果最好;酶液保存时间在4 h内最佳;-20℃保存比4℃保存对酶活性影响小。最佳检测条件为:取样量为1 mL时,反应温度为30℃,反应时间为20 min时,SOD酶活性最大。