土壤有机质含量测定方法的改进研究

通过研究改进了土壤有机质含量的测定方法。首先称取适量土壤置于长管消解系统中进行消解,然后采用全自动电位滴定仪进行滴定,直接获得土壤的有机质含量。使用该方法测定的土壤标准样品的有机质含量均在保证值以内,同时对实际样品进行精密度测试,得到相对标准偏差为1．03％。该方法降低了土壤有机质含量检测的实验成本,减少了环境污染,同时提高了实验数据的准确度与精密度,值得推广。     

Effect of nitrite on hydrolysis-acidification, biogas production and microbial community in semi-continuous two-phase anaerobic digestion of sewage sludge

Previous study found that the pre-treatment of sewage sludge with nitrite improves the biogas production during the mono/two-phase anaerobic digestion (AD) using batch biochemical methane potential tests. In this study, the effects of nitrite on hydrolysis-acidification, biogas production, volatile solids destruction and microbial composition in semi-continuous two-phase AD of sewage sludge were investigated. The addition of nitrite promotes sludge organic matter solubilization (+484%) and VFAs production (+98.9%), and causes an increase in the VS degradation rate during the AD process (+8.7%). The comparison of biogas production from the acidogenic and methanogenic reactors with or without the addition of nitrite implies that the nitrite has no significant effect on the overall biogas production of two-phase sludge AD process. High-throughput sequencing analysis shows that the microbial communities of bacteria and archaea in two-phase AD reactors significantly changes after the addition of nitrite. Vulcanibacillus (bacteria) and Candidatus Methanofastidiosum (archaea) become the dominant genera in the acidogenic and methanogenic reactors with the nitrite respectively. These findings provide new insights about using nitrite to promote the organic matter degradation of sewage sludge in a semi-continuous two-phase AD system.     

Performances of mesophilic anaerobic digestion systems treating poultry mortalities

Abstract

A closed‐loop anaerobic digestion system consisting of a leachbed (LB) and an upflow anaerobic sludge blanket (UASB) was tested as an alternative for the disposal of poultry mortalities. This paper compares the performances of three LB‐UASB treatment systems with different initial moisture contents in the LBs. Each LB was loaded with one chicken and 5, 10 or 18 liters of water. The LBs initially carried out the hydrolysis/acidification phase while the UASBs the methanogenesis phase. Due to repeated inoculation by the UASBs, the LBs with 10 and 18 liters of water started producing methane on day 5, while the one with 5 liters of water on day 19. However, methane production rates were low before day 40 for the LB with 10 liters of water and day 60 for the other LBs. Methane production gradually improved as the LBs continued to receive ungranulated sludge from the UASBs. The LBs eventually became balanced methane reactors. Continued balanced fermentation in the LBs resulted in leachates with very low substrate concentrations that could no longer support high‐rate methanogenesis in the UASBs. Consequently, methane production rates from the UASBs decreased quickly while that from the LBs reached peak levels. Cumulative methane production from each LB eventually exceeded that from its connecting UASB. After 118 days of digestion, 414, 437 and 470 liters of methane were produced from the three systems, respectively. Cumulative methane production from the LBs with 5 and 18 liters of water accounted for 63% of the total methane produced from their respective systems. The LB with 10 liters of water produced 75% of the total methane from that system. Methane yields ranged from 0.485 to 0.554 m³ (Kg TS) ¹. About 86% of the initial dry weight was biodegraded. All three systems performed very well with little operational problems. Overall, the system that started with 10 liters of water in the LB performed the best. Strategy for enhancing system performances and implementing farm applications are discussed.     

基于PCR-TGGE技术的餐厨垃圾厌氧消化微生物群落结构解析

为了解不同负荷下单相餐厨垃圾厌氧消化反应器内微生物群落结构演替特征,在单相厌氧消化反应器负荷为2.0～8.5kg·m-·3d-1(以VS计)的不同负荷条件下取样,运用16SrDNA的PCR-TGGE技术对反应器内微生物进行动态追踪.同时,运用Dice系统和NMDS软件对PCR-TGGE图谱进行分析.结果表明,负荷为4.0～6.0kg·m-·3d-1时,微生物群落结构变化不大;负荷为6.0～7.0kg·m-·3d-1时,微生物群落结构变化较为明显;负荷分别为7.0～8.0kg·m-·3d-1及8.5kg·m-·3d-1时,微生物群落结构变化最为明显.纵观整个过程,在餐厨垃圾厌氧消化反应器有机负荷在2.0～8.5kg·m-·3d-1下厌氧反应器内的微生物群落结构存在明显的阶段性演替;负荷为7.0kg·m-·3d-1时微生物群落结构的丰富度最好.     

梯度负荷下果蔬垃圾厌氧消化性能及微生物群落结构的研究

为优化果蔬垃圾厌氧消化工艺,提高厌氧消化性能,本文通过逐级提高CSTR反应器进料负荷,研究不同负荷下的厌氧消化性能及相应的微生物群落结构变化规律.结果表明,随着进料负荷的增高,容积产气率、甲烷产气量、氨氮、碱度、TCOD、SCOD均逐渐增高,在最高负荷(负荷以VS计)2.50g·L-·1d-1时分别达到最大值:1.22L·L-1d-1,5.10L·d-1,1563.86mg·L-1,7572.23mg·L-1,13283.26mg·L-1,2075.03mg·L-1,甲烷含量及VFA分别稳定在52.46%～54.59%和(879.30±18.69)mg·L-1;同时利用PCR-DGGE技术系统分析了厌氧消化中细菌与古细菌的群落结构,测序结果表明,整个过程中拟杆菌(Bacteroidetes)、甲烷鬃菌(Methanosaeta)及甲烷螺菌(Methanospirillum)为优势微生物,随着负荷的提高,甲烷鬃毛菌(Methanosaeta)活性逐渐降低;聚类分析及主成分分析表明,低负荷条件下(1.50g·L-·1d-1、1.75g·L-·1d-1),微生物种类(细菌、古细菌)差别不明显,且基本处于同一阶段.     

有机固体废弃物厌氧干发酵机制研究进展

利用厌氧干发酵技术处理固体有机废物与传统的湿发酵相比具有许多优势,但厌氧干发酵机制的研究存在许多困难,在一定程度上限制了厌氧干发酵技术的发展。文章在对国内外研究现状进行文献调查后,总结概括了厌氧干发酵理论模型从"两点模型"和"区反应模型"到"浓度波扩散模型"和"反应前沿假说"的发展进程,讨论了其各自特点和对厌氧干发酵机制研究的意义以及其不完善之处;并分别从微生物生长、底物水解和生物气产生三个方面综述了近年来国内外对厌氧干发酵动力学的研究进展。然而,目前的研究仅是针对某些物料进行的特异性研究,还没有一个普遍适用的关于有机固体废弃物厌氧干发酵的理论模型被发展出来,因此对干发酵传质传热机制的探索和数学模拟成为当前对于干发酵机制研究的主要方向。     

手提式蒸汽消毒器同时消解总磷总氮实验分析

水体中总磷、总氮的增多,会造成藻类的滋生,使水环境质量降低。因此,对总磷、总氮的监测十分必要。国标方法测定水中总磷总氮,都要用手提式蒸汽消毒器进行消解,且消解温度和时间相同。为建立一种快速的测定方法,将总磷、总氮同时放入蒸汽消毒器中进行消解,将此方法与标准消解法进行了对比分析。结果表明:同时消解法的精密度、准确度、回收率、工作曲线等均符合总磷总氮的测定要求,标准物质的测定结果和相对误差均在规范范围内,说明此方法可靠。在总磷、总氮都需检测时,大大缩短了实验时间,减少了蒸汽消毒器的使用频率,是一种快速、简便测定水中总磷总氮的方法。     

微波法快速测定脱硫石膏的主次量元素

采用混合酸微波加热消解、ICP-AES法测定电厂脱硫副产物石膏的多种元素成分,与常规方法 GB/T5484-2000相比较简便快速,准确度高。     

产甲烷抑制剂氯仿对污泥厌氧消化中同型产乙酸作用的影响

厌氧消化是城市污泥常用的资源化处理方式,添加产甲烷抑制剂得到的发酵产物乙酸相比于甲烷被认为更具附加值.同型产乙酸途径是污泥厌氧发酵产乙酸途径之一,然而产甲烷抑制剂的存在对其影响尚不明确,这对污泥厌氧发酵产酸工艺的优化和应用至关重要.本文研究了不同氯仿浓度抑制产甲烷条件下挥发性脂肪酸、气体浓度及同型产乙酸菌和总细菌数量的变化,基于乙酸的稳定性碳同位素分馏效应分析了不同温度条件下氯仿对同型产乙酸作用的影响.结果显示,0.1%和0.5%(V/V)氯仿浓度条件下最高乙酸浓度分别为24.5和22.4 mmol·L~(-1),远低于对照组的52.6 mmol·L~(-1).氯仿抑制产甲烷条件下乙酸的稳定碳同位素丰度δ~(13)C值均高于污泥有机质的δ~(13)C值,50℃时乙酸的δ~(13)C值最高,且同型产乙酸菌相对丰度也低于15和30℃条件下.可见,产甲烷抑制剂氯仿同时能够抑制同型产乙酸作用,0.5%浓度下的抑制效果高于0.1%浓度下,且50℃条件下其抑制作用强于15和30℃条件下.     

Effect of manganese oxide-modified biochar addition on methane production and heavy metal speciation during the anaerobic digestion of sewage sludge

Low organic matter content and high heavy metal levels severely inhibit the anaerobic digestion (AD) of sewage sludge. In this study, the effect of added manganese oxide-modified biochar composite (MBC) on methane production and heavy metal fractionation during sewage sludge AD was examined. The MBC could increase the buffering capacity, enhance the methane production and degradation of intermediate acids, buffer the pH of the culture, and stabilize the sewage sludge AD process. The application of MBC positively impacted methane production and the cumulative methane yield increased up to 121.97%, as compared with the control. The MBC addition can improve metal stabilization in the digestate. An optimum MBC dose of 2.36?g was recommended, which would produce up to 121.1?L/kg volatile solids of methane. After the AD process, even though most of the metals accumulated in the residual solids, they could be transformation from the bio-available fractions to a more stable fraction. The total organic- and sulfide-bound and residual fraction content at a 3?g dose of MBC that is 0.12?g/g dry matter were 51.06% and 35.11% higher than the control, respectively. The results indicated that the application of MBC could improve the performance of AD and promote stabilization of heavy metals in sewage sludge post the AD process.