城市垃圾好氧堆肥处理的几个关键问题

介绍了城市垃圾好氧堆肥过程的几个关键问题，分析了堆肥过程中的微生物特性，提出以耗氧速率、C／N作为堆肥腐熟度综合判定指标。并简单介绍了国外应用较多的温度、氧浓度自动控制系统。     

城市污泥好氧堆肥过程中重金属的形态转化

城市污泥是一种富含作物生长需要的多种养分的生物固体废弃物,但重金属问题又成为影响污泥农用的关键因素,而重金属的生物活性、迁移性及毒性不仅取决于总量,很大程度上取决于其存在的形态.该实验通过调节城市污泥的水分和C/N比,利用笔者所在课题组自行开发的好氧堆肥反应器进行城市污泥堆肥处理,经过为期20 d的好氧堆肥处理,研究堆肥前后污泥中的重金属总量和化学形态的变化.实验结果表明:堆肥处理由于添加能源调理剂等,使堆肥产品中的重金属含量低于原污泥,符合了农用污泥污染物控制标准;同时堆肥也改变了重金属的化学形态,降低了剧毒性的Cd的生物有效性.对污泥及堆肥的重金属形态研究发现:大部分重金属主要以残渣态形式存在,生物毒性很小,农用时的重金属污染度也很低.     

磷酸盐添加对快速好氧堆肥过程pH及腐熟效果的影响

随着我国环保政策的日趋严格,具有堆肥周期短、产品质量好、二次污染小等优点的反应器快速好氧堆肥工艺受到人们的广泛关注.然而,由于堆肥原料的有机物含量高,导致快速堆肥初期的有机酸累积,堆体pH偏低,影响堆肥效果.本研究拟通过添加磷酸盐,解决剩余污泥反应器快速堆肥过程出现的pH偏低问题.结果表明,添加磷酸盐可有效控制堆体pH,堆肥初期,HPO_4~-通过与有机酸解离产生的H~+反应生成H_2PO~-_4,提高堆体pH,堆肥后期,蛋白质降解产生较多NH~+_4,导致pH升高,堆体中的H_2PO~-_4通过与OH~-结合生成HPO_4~-,降低堆体pH.当HPO_4~-与H_2PO~-_4的摩尔比为2∶5时,堆体pH值可维持在6.0—8.5之间,有机物降解率最高,堆体的NH~+_4-N含量最大,达3.99 mg·g~(-1),堆肥过程的保氮效果较好,且所得堆肥产品的种子发芽指数也较高,腐熟程度良好.     

微生物菌剂堆肥中草药渣中试研究北大核心CSCD

木质纤维素降解是中草药渣堆肥的主要难点.在前期小试的基础上,接种纤维素降解菌剂,将1 t新鲜药渣直接进行好氧堆肥.腐熟度指标T值和种子发芽指数(GI)显示,堆肥19 d左右就已经腐熟.堆肥过程中接种组(JZ)和对照组(CK)的纤维素平均降解速率分别为0.73 kg/d和0.64 kg/d,JZ比CK纤维素降解总量提高了13.39%,木质素降解量提高118.18%.第30天时,堆肥的含水率、p H、总养分、重金属等指标都达到有机肥料标准(NY 525-2012).接种菌剂提高了堆肥温度,加速了水分散失,促进了纤维素和木质的转化,有利于堆肥腐熟和提高肥料品质.因此,在中试规模上堆肥中草药渣生产有机肥是可行的.     

剩余污泥好氧堆肥生产有机复混肥的肥分及效益分析

城市污水处理厂剩余污泥含有大量有机质和氮、磷等营养元素,是农业生产宝贵的肥源。将污泥制成有机复混肥可以使作物增产,并改善土壤结构、提高土壤肥力。     

粪渣污泥好氧堆肥过程中主要理化性质的动态变化

进行了粪渣污泥的强制通风静态垛堆肥试验,分析了温度、氧气、含水率和挥发性有机物在堆肥不同阶段的变化特征。粪渣与木屑质量1∶1.5的比例下,能够实现快速高温好氧堆肥,堆体温度在高温期持续9d,达到无害化的卫生学要求。堆体耗氧速率在升温阶段后期上升到最大值,此后持续降低,到堆肥后期趋于稳定。据此提出了相应的通风策略。在堆肥过程中,物料的含水率和挥发性有机物含量持续降低,但到堆肥后期趋于稳定,堆肥结束时分别减小17个百分点和10.4个百分点。     

钝化剂对好氧高温堆肥处理猪粪重金属含量及形态的影响

采用连续提取法研究猪粪好氧堆肥处理中钝化剂对重金属含量及形态的影响.结果表明:堆肥处理后,猪粪中重金属Zn、Cu、Pb、Cr和As普遍升高,重金属Hg明显降低;堆肥处理能促进猪粪中重金属Zn、Cu、Pb、Cr、As和Hg的形态向活性低的方向转化,降低重金属的生物有效性.在3种重金属钝化剂处理中,沸石处理对降低猪粪中重金属Zn的生物有效性效果最好;海泡石处理对降低猪粪中重金属Cu和Cr的生物有效性效果最好;膨润土处理对降低猪粪中重金属Pb和Hg的生物有效性效果最好.因此沸石、海泡石和膨润土处理有利于降低猪粪施用中的重金属污染风险.     

发酵基质含水率对牛粪好氧堆肥发酵产热的影响

以牛粪和玉米秸秆为原料进行好氧堆肥试验,采用氧弹量热法测定发酵产热量,研究堆肥原料不同初始含水率(物料初始含水率w分别为41%、50%、55%、65%和75%)对发酵产热的影响,以及堆肥过程中有机质损失与产热的关系。结果表明,在堆肥第3天各处理(除初始含水率75%处理)温度均达55℃以上,堆肥各处理均表现为前3 d有机质降解最快,热值损失最多。物料初始含水率为41%～65%时,发酵产热量与物料初始含水率呈显著正相关。初始含水率65%对堆肥最有利,有机质损失和总热值变化最大,有机质损失29.18%,总产热量为2 236 kJ.kg-1,若所产热量全部用于去除水分,可以使堆肥物料水分完全去除。     

新型调理剂CTB-2污泥堆肥的氧气时空变化特征研究

采用新型CTB-2调理剂与城市污泥进行堆肥,研究了堆肥过程中氧气、温度的时空变化特征。结果表明,m（CTB-2调理剂）：m（污泥）=1：2能够有效降低污泥容重,改善堆体结构;堆体能够快速升温至高温期并持续7d以上,最终完成无害化;采用该比例的调理剂能够保证堆体的通风供氧,使堆体各层通风后的氧气体积分数都恢复至19％以上,最低氧气体积分数维持在数17％以上;堆肥过程中堆体的氧气体积分数、耗氧速率和温度都具有明显的层次效应,堆体耗氧速率呈先升高后降低的趋势,堆体通风后的氧气和最低氧气体积分数均随着堆肥的进行而增加。     

造纸污泥工厂化堆肥过程中理化性质的动态变化

工厂化强制通风静态垛好氧堆肥试验结果表明,造纸污泥与木屑按10∶1比例混合后,2~3 d即可达到60℃,高温期维持时间超过10 d,完全符合我国标准CJJ/T52-93规定,达到无害化要求;堆肥过程中堆体上层温度大于下层;高温堆肥后物料含水率降低20.2%,脱水效果明显;造纸污泥堆肥过程中物料的挥发性固体持续降低;堆体耗氧速率在升温阶段后期上升到最大值,此后持续降低,到堆肥后期趋于稳定。     

堆肥过程中有机质和微生物群落的动态变化

利用3个容积约为50 L的平行生物反应装置研究堆肥过程中温度、湿度（水分含量）、pH值和有机质的动态变化情况。按照Van Soest方法根据有机质不同的溶解特性将其分为：溶于沸水的有机质H2O、溶于中性试剂的有机质SOLU、半纤维素（HEMI）、纤维素（CELL）和木质素（LIGN）。结果表明：反应装置内环境湿度调控在60%左右时,堆肥系统内借助生化反应,温度最高可达到约50℃。堆肥材料在反应初期呈现偏酸性（pH=6.5）,而随着反应的发生,pH逐渐变为中性或弱碱性（pH=7.4）。经过20 d的堆肥实验,有机质总量降解了约47%。在微生物作用下的各类有机质的降解率不同,按大小排序为H2O〉HEMI〉CELL〉SOLU〉LIGN,其降解率分别是85%、56%、36%、32%和27%。为了深入理解堆肥过程中有机质的降解机制,文章采用磷脂脂肪酸（PLFAs）技术对体系中的微生物群落变化进行了初步分析,发现微生物优势群落随反应温度的改变发生明显变化,在堆肥初期和堆肥中期,细菌占优势,而堆肥末期时真菌比例较高。在堆肥的过程中,革兰氏阴性菌的比例呈下降趋势,而革兰氏阳性菌的比例呈上升趋势。     

Nitrogen-retaining property of compost in an aerobic thermophilic composting reactor for the sanitary disposal of human feces

Aerobic composting is a method for the sanitary disposal of human feces as is used in bio-toilet systems. As the products of composting can be utilized as a fertilizer, it would be beneficial if the composting conditions could be more precisely controlled for the retention of fecal nitrogen as long as possible in the compost. In this study, batch experiments were conducted using a closed aerobic thermophilic composting reactor with sawdust as the bulk matrix to simulate the condition of a bio-toilet for the sanitary disposal of human feces. Attention was paid to the characteristics of nitrogen transformation. Under the controlled conditions of temperature at 60°C, moisture content at 60%,anda continuous air supply, more than 70% fecal organic removal was obtained, while merely 17% fecal nitrogen loss was observed over a two-week composting period. The nitrogen loss was found to occur mainly in the first 24 h with the rapid depletion of inorganic nitrogen but with an almost unchanged organic nitrogen content. The fecal NH₄-N which was the main component of the inorganic nitrogen ( > 90%) decreased rapidly in the first day, decreased at a slower rate over the following days, and finally disappeared entirely. The depletion of NH₄-N was accompanied by the accumulation of NH₃ gas in the ammonia absorber connected to the reactor. A mass balance between the exhausted NH₃ gas and the fecal NH₄-N content in the first 24 hours indicated that the conversion of ammonium into gaseous ammonia was the main reason for nitrogen loss. Thermophilic composting could be considered as a way to keep a high organic nitrogen content in the compost for better utilization as a fertilizer.     

Environmental effects and risk control of antibiotic resistance genes in the organic solid waste aerobic composting system: A review

• ARGs were detected in livestock manure, sludge, food waste and fermentation dregs. • The succession of microbial community is an important factor affecting ARGs. • Horizontal transfer mechanism of ARGs during composting should be further studied. Antibiotic resistance genes (ARGs) have been diffusely detected in several kinds of organic solid waste, such as livestock manure, sludge, antibiotic fermentation residues, and food waste, thus attracting great attention. Aerobic composting, which is an effective, harmless treatment method for organic solid waste to promote recycling, has been identified to also aid in ARG reduction. However, the effect of composting in removing ARGs from organic solid waste has recently become controversial. Thus, this article summarizes and reviews the research on ARGs in relation to composting in the past 5 years. ARGs in organic solid waste could spread in different environmental media, including soil and the atmosphere, which could widen environmental risks. However, the conventional composting technology had limited effect on ARGs removal from organic solid waste. Improved composting processes, such as hyperthermophilic temperature composting, could effectively remove ARGs, and the HGT of ARGs and the microbial communities are identified as vital influencing factors. Currently, during the composting process, ARGs were mainly affected by three response pathways, (I) “Microenvironment-ARGs”; (II) “Microenvironment-microorganisms-ARGs”; (III) “Microorganisms-horizontal gene transfer-ARGs”, respectively. Response pathway II had been studied the most which was believed that microbial community was an important factor affecting ARGs. In response pathway III, mainly believed that MGEs played an important role and paid less attention to eARGs. Further research on the role and impact of eARGs in ARGs may be considered in the future. It aims to provide support for further research on environmental risk control of ARGs in organic solid waste.     

菌剂对堆肥的作用及其应用

好氧高温堆肥是一种受微生物控制的有机物降解和转化的过程。在堆肥过程的不同阶段对有机物降解起关键作用的微生物种群不同。接种菌剂可以使堆肥物料快速达到高温、控制堆肥过程中臭气的产生，缩短堆肥腐熟进程；可以有效杀灭病原体和降解有机污染物，提高堆肥质量。堆肥产品含有生物活性的微生物，作物增产效果显著。文章总结了接种菌剂在堆肥过程中的作用和应用效果，提出接种菌剂的研究首先应利用传统微生物研究法和先进的分子生态学技术摸清堆肥过程中微生物活动规律，逐步筛选出所需功能性菌群，在堆肥应用时要确定菌剂的最佳接种时间和接种量。     

木薯皮堆肥过程中酶活性的变化

以木薯皮为原料进行高温堆肥发酵,研究了堆肥化过程中理化性质和酶活性的变化情况.结果表明:在堆肥发酵过程中.温度变化呈先上升后下降趋势,到后期已趋近于初始温度;而含水率在堆肥处理过程中变化不大.各处理的pH值在发酵结束时为7.3～7.5.过氧化氢酶活性初期较高,随后迅速降低,并维持在较低水平.纤维素酶和脲酶活性在堆肥初期增加,之后逐渐降低.由于堆肥原料不同,不同处理的酶活性变化趋势表现出一定的差异.考虑到堆肥腐熟度受多方面因素的影响,判断堆肥腐熟度时应根据多种指标(包括生物学、化学、物理学指标)综合判断.     

Degradation of sulfonamides during anaerobic composting of swine manure

Residual antibiotics in manure pose a potential threat to public and ecological health as a result of the application of manure from animals treated with antibiotics to land. The environmental fate of sulfonamides (SAs) in swine manure after composting and field application remains largely unknown. We studied the degradation of the antibiotics sulfadiazine (SD), sulfathiazole (ST), and sulfamethazine (SM2) during anaerobic composting. We tested the effects of temperature and antibiotic concentration on degradation rates. We also evaluated the changes in pH, moisture, and biological degradation material in manure spiked with SAs and in a control. Results showed that the 3 SAs decreased by between 52.31% and 90.30% in all 9 treatments following 14 days of anaerobic composting, and the highest removal efficiencies were observed at a temperature of 35°C and initial concentrations of 6.03, 6.48, and 6.32?µg/g of SD, ST, and SM2, respectively, which were degraded by 90.30%, 85.78%, and 75.18%. Removal efficiencies for all SAs correlated well with moisture and biological degradation material of the manure. These results indicate that composting may be a practical and effective way to reduce concentrations of these three SAs in swine manure prior to its land application.     

猪粪混合堆肥过程中重金属含量的变化

在猪粪混合堆肥中，采用不同的通风方式和填充料，分析该过程中重金属总量和DTPA提取的重金属含量变化。结果表明，通过猪粪混合堆肥，重金属总量不会降低，但重金属生物有效性可降低；在猪粪与木屑混合堆肥中，加入树叶或鸡粪均能显著降低重金属的生物有效性，强制通风 机械翻堆比单一机械翻堆更能降低重金属的生物有效性。     

微生物混合堆制法处理油污土壤的净化效果

堆制处理工艺是处理油污土壤的一种强化的生物处理工艺。在两种油污土样的堆制中投加了四株高效石油降解菌,处理60d后考察投加了混合菌的净化效果,主要包括油污中饱和烃、芳香烃、胶质、沥青质、总烃碳数组分相对含量的变化以及土壤中重金属含量及其水溶性的变化。结果表明:饱和烃的绝对去除量以及去除率都要高于其它三者;土样1和土样2总烃碳数组分百分比的变化幅度差别较大,呈现低碳数下降、高碳数升高的趋势,可见添加的高效石油降解菌以利用中低碳数烃类为主;该复合微生物堆制处理法对土壤的重金属污染基本无影响。