Non-destructive study on identifying and monitoring of Cu-Pb pollution in corn based on near-infrared spectroscopy

Environmental Science and Pollution Research - The problem of heavy metal pollution in the environment is of increasing concern, especially in the agricultural environment. In this study, a method...     

短程硝化的实现、维持与过程控制的研究现状

短程生物脱氮技术目前倍受人们的关注,国内外学者对短程硝化提出了多种实现及维持的控制途径,但仍存在着一些问题。由于活性污泥法中DO,ORP,pH的变化规律从不同角度不同程度地反映了生物脱氮反应的进程,所以用它们作为控制参数就可以对生物脱氮反应进行过程控制。在分析中,通过对国内外短程硝化控制途径的研究现状与发展趋势的分析和总结,针对目前在实现短程硝化及维持短程硝化各种途径中存在的问题,提出了通过在线检测DO,pH,ORP来实现与维持短程硝化的新思路。     

上流式缺氧污泥床和好氧生物膜组合脱氮工艺的研究

将上流式颗粒污泥床(USB)用于反硝化和生物膜法用于自养硝化处理蔗糖配水和小区生活污水,反硝化污泥床去除有机物和硝态氮具有节省需好氧去除有机物的能耗的优势,同时好氧生物膜法硝化效率高。试验结果表明,当工艺进水的有机负荷小于2kgCOD/m3·d时,出水COD均小于60mg/L,好氧单元进水有机负荷和氨氮负荷分别小于13kgCOD/m3·d和09kgNH3N/m3·d时,出水氨氮小于5mg/L;COD/NO-3N是影响反硝化的关键因素,处理蔗糖配水时,COD/NO-3N大于5时反硝化脱氮完全,而COD/NO-3N为10时,生活污水作为电子供体仍然脱氮不完全;有机物含量过高导致好氧单元硝化效果降低,HRT是影响好氧单元硝化效率的主要因素,HRT缩短为15h时,氨氮去除率降低了85%左右;同时处理蔗糖配水和生活污水的反硝化菌活性相当。     

关于亚硫酸钙氧化过程中一些问题的探讨

介绍了亚硫酸钙氧化为石膏的反应机理及影响反应过程的某些因素。对某厂工程实践中出现的问题进行了解释,并提出了指导性建议。     

基于秸秆后发酵产沼气的一次发酵时间优化

采用"一次发酵+NaOH处理+二次发酵"工艺,以稻秸为原料,研究一次发酵时间对稻秸沼气发酵的影响.结果表明,一次发酵后的稻秸仍有一定的产气能力,干物质(TS)产气量为28.11～50.73mL/g TS,产气量大小与一次发酵时间成反比;一次发酵后的稻秸经NaOH处理后,稻秸物质结构受到明显破坏,有机物大量溶出,稻秸浸提...     

非接触式超声波局放检测仪校验平台研究

非接触式超声波局放检测仪缺乏统一的性能校验平台,影响电力设备局放检测结果的有效性和可靠性,在现有接触式超声波检测平台校验基础上,建立了相应的非接触式超声波局放检测装置校验平台,并提出了模拟装置,实验室环境联合校验方法。所述的校验方法具有稳定性高,重复性好的特点,弥补了非接触式超声波局部放电检测仪在空间,实用性与理想环境差异等问题,有一定的参考价值。     

基于习性和食物网的白洋淀大型底栖动物群落恢复研究

白洋淀由于长期受人类活动影响,部分区域内源污染严重.针对该类区域,"十三五"水专项开展了生态清淤试点工程以实现内源治理.在清淤过程中底栖生物容易遭到严重破坏,与之密切联系的食物网受到影响.在沉水植物补种成功后,如何科学地恢复底栖动物群落并维持长效稳定,急需寻求解决方案.本研究于2018年对白洋淀大型底栖动物群落进行调查,根据调研结果、习性特征和食物网模型,提出了受损后大型底栖动物群落恢复方案.研究发现,春季优势种为螺类软体动物和虾类甲壳类动物,夏季和秋季为螺类软体动物和昆虫类摇蚊幼虫.全年主要优势种为中华圆田螺、中国圆田螺、羽摇蚊和大红德永摇蚊.通过食物网模型计算,确定了软体动物是2010年和2018年的关键功能组.因此,综合优势种和关键种,底栖动物群落恢复物种主要选择虾类、螺类和摇蚊幼虫.根据底栖动物的习性,确定甲壳动物和摇蚊幼虫以自然恢复为主,螺类以人工恢复为主的恢复方式.针对螺类关键物种,根据2018年调研生物量、工程经验值和生态容量综合确定其恢复投加量合理范围.通过以上研究,建立了基于食物网成熟度和稳定性的底栖动物群落恢复优化调控方案,为受损底栖动物群落的恢复提供借鉴.     

微塑料对双齿围沙蚕生理代谢的影响研究

为探讨微塑料对双齿围沙蚕生理代谢的影响,本文研究了聚丙烯(PP)、聚酰胺(PA)和聚氯乙烯(PVC)3种微塑料在不同浓度(0.1％、1％和5％)和暴露时间下对双齿围沙蚕体内过氧化氢酶(CAT)、乙酰胆碱酯酶(AchE)活性以及代谢指标排氨率和呼吸速率的影响.结果表明,随微塑料浓度的升高,双齿围沙蚕体内CAT活性显著提升,5％浓度下双齿围沙蚕体内CAT活性最高;PVC对双齿围沙蚕体内AchE活性表现为低浓度(0.1％)抑制、高浓度(5％)促进的作用;PP和PA在不同浓度下对双齿围沙蚕体内AchE酶活性均表现为促进作用;随着微塑料浓度的升高,双齿围沙蚕的排氨率和呼吸速率显著升高(P<0.05).综上,微塑料在高浓度条件下,在一定时间内可以对双齿围沙蚕产生氧化胁迫作用,并一定程度上影响其排氨率和呼吸速率.     

Sewage sludge ditch for recovering heavy metals can improve crop yield and soil environmental quality

• Indirect use of sludge in ditches alongside plants was tested in field experiments. • The dried and stabilized sludge in ditches was recovered with heavy metals. • Cd, Pb, Cu and Zn in the planted soil were all in a safe range. • The indirect use of sludge increased plant yield, soil N content and C storage. The treatment and disposal of municipal sewage sludge (MSS) is an urgent problem to be resolved in many countries. Safely using the nutrients within MSS to increase crop yield and enhance the fertility of poor soil could contribute to achieving sustainable development. An indirect use of MSS in ditches alongside Pennisetum hybridum plants was studied in field plots for 30 months and the contents of heavy metals and macronutrients were monitored in soil, sludge and plant samples. We found that the yield of P. hybridum was significantly increased by 2.39 to 2.80 times and the treated plants had higher N content compared with no sludge. In addition, the organic matter (OM) and N contents in the planted soil increased significantly compared with the initial soil. The OM content in the planted soil of the MSS treatment was 2.9 to 5.2 times higher than that with no sludge, and N increased by 2.0 to 3.8 times. However, MSS had no significant effect on the N, P and K contents in the soil at the bottom of the MSS ditch, and the content of heavy metals (Cd, Pb, Cu and Zn) were also within the safe range. Moreover, the moisture content and phytotoxicity of MSS after this indirect use were reduced and the heavy metal contents changed little, which is favorable to the further disposal of recovered MSS. Therefore, this indirect use of MSS is beneficial to agricultural production, soil quality and environmental sustainability.     

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.