有机废物堆肥中的微塑料污染:来源、相互作用及展望

微塑料作为新型污染物,近年来受到高度关注。堆肥作为一种广泛使用的有机废物处理技术,对微塑料具有一定的降解作用。目前,关于堆肥中微塑料污染的研究少之又少,但微塑料隐藏在堆肥中并随堆肥进入土壤环境的危害已初见端倪。一方面,微塑料改变堆肥微环境,影响微生物多样性,降低堆肥品质;另一方面,在堆肥过程中,微塑料降解释放内源性有毒物质,且其表面可吸附重金属和有机污染物等,可能导致复合污染效应。从堆肥产品中微塑料的污染情况、对堆肥的影响、堆肥对微塑料的降解作用与改良方法等方面进行了系统综述,结合不同种类微塑料在堆肥中的降解情况,提出目前可生物降解塑料存在的问题,展望堆肥中微塑料研究的未来发展方向。     

土壤中有机农药的自然降解行为

有机农药是一类典型的环境污染物,自然降解是其在土壤中消除的主要过程。本文阐述了土壤中有机农药生物降解、光解、水解和化学氧化等自然降解机制,综述了土壤中有机农药自然降解的研究方法及研究现状,指出了目前自然降解研究中存在的一些问题并展望了今后的研究方向。     

持久性有机污染物的根际修复及其研究方法

根际是具有特殊性质的土壤微生态环境,对土壤中持久性有机污染物的行为及生物修复具有重要作用。本文从微生物降解、植物过程、非生物降解、土壤吸附、挥发、淋溶等方面归纳了有机污染物根际修复的研究进展,并从细胞培养、添加根系分泌物或根系残留物、挥发污染物收集和残留态污染物测定等方面综述了有机污染物根际行为的研究方法及其优缺点。     

城市污泥堆肥过程中有机污染物的变化

根据国内外研究资料，综述了城市污染在堆肥处理过程中氯代酚（CPs)、PCDD/Fs、多环芳烃（PAHs)类、氯苯类（PCBs、CBs)等有机污染物的变化，提出将城市污泥进行堆肥处理，可以不同程度降解其中各种有机污染物，达到农用的目的。有机污染物降解的效果与其种类和性质、污泥的性质、环境因素（包括微生物类型和数量、C／N比、水分含量、温度、通气状况）等有关。     

微生物响应PBAT-PLA生物降解膜袋工业需氧堆肥降解机制

塑料污染已对全球环境造成严重威胁,生物降解塑料的推广使用及其工业堆肥是治理塑料污染的有效途径之一。该研究根据标准GB/T 19277.1-2011,在（58±2）℃的特殊高温条件下,对PBAT-PLA生物降解膜袋进行有氧堆肥降解,并选择微晶纤维素作为对照。通过对堆肥中的微生物进行16S/18S高通量测序,分析降解过程中细菌/真菌的群落种类和数量变化,包括物种多样性、物种组成、物种差异分析、样本比较分析,并结合扫描电镜下的微观形貌,深入探寻可降解塑料膜袋在工业需氧堆肥过程中的微生物响应降解机制。结果表明：微晶纤维素和生物降解膜袋在降解活跃期（第140天取样）,其所在堆肥中大量存在的优势菌属为Sphaerobacter（球杆菌属,放线菌纲）,分别占比20.25%和39.44%。与同样条件下不含降解材料的对照组堆肥相比,微晶纤维素/生物降解膜袋工业需氧堆肥降解过程中显著增长的4种菌属中有3种属于放线菌,说明放线菌对聚酯物的解聚以及纤维素的降解具有积极的作用。试验结果也表明了聚酯和纤维素的完整生物降解过程不依赖单一菌种,而是微生物协同作用的结果。     

有机固废堆肥过程的水分平衡模型研究进展

畜禽粪便等有机固体废物堆肥过程中水分含量影响堆肥反应过程,并最终影响堆肥产品质量和后续的产品加工,建立堆肥过程中的水分平衡模型有利于深入理解堆肥过程并优化堆肥过程的工艺参数。该文基于国内外研究进展,对堆肥模型建立基础、水分模型及有机质降解模型研究现状进行综述,概括了堆肥过程中水分迁移转化的主要途径,明确了堆肥过程有机质降解产生的水分是水分平衡模型的重要组成部分。同时,提出可以根据物料平衡思想建立堆肥过程中质量平衡模型,由此分析了堆肥过程中水分平衡模型和有机质降解模型。现在的水分质量平衡模型考虑了堆肥过程中通风对流、水汽蒸发以及微生物作用有机质降解产水对水分的影响,将水分模型分为对流模型、反应—对流模型、反应—蒸发模型和反应—对流—扩散模型4种模型。堆肥产水过程中的有机质降解模型主要有一阶动力学模型、Monod模型和经验模型。     

铜绿假单胞菌生物降解特性的研究进展

近年来在环境污染物的生物降解研究方面有了很大进展。铜绿假单胞菌（Pseudomon aslugtrlosa,PA）作为重要的降解菌株之一,具有较强的降解能力,可降解物质种类广泛,在环境污染物的生物降解中具有重要作用并占据重要地位。本文综述了PA的降解特性、代谢途径、遗传基础与酶系及促降解物质在生物降解方面的研究进展。     

土壤环境中多环芳烃的微生物降解及联合生物修复

研究土壤环境中持久性有机污染物的生物降解及其生物修复技术是当今国际环境修复科学技术前沿领域的重要课题。本文重点论述了土壤环境中持久性有机污染物多环芳烃的微生物降解机理及其在生物修复中的应用等,并结合当前研究进展,展望了基于多种修复措施相结合的多环芳烃污染土壤联合生物修复工程技术的开发与应用前景。     

木质纤维素降解菌剂DN-1促进堆肥腐熟度的评估

为提高堆肥中木质纤维素降解效率,促进堆肥腐熟进程,主要采用红外光谱法(FTIR),同时结合堆肥温度、种子发芽率及木质纤维素含量变化,研究了添加木质纤维素降解菌剂DN-1对堆肥腐熟的促进作用。结果表明,加入菌剂使堆肥在45℃以上高温期持续20 d,比自然堆肥高温期延长6 d;堆肥结束时,添加菌剂堆肥的种子发芽指数为93.3%,自然堆肥仅为56.7%;菌剂堆肥中木质素、纤维素和半纤维素的降解率分别为42.54%、62.57%和67.14%,分别高出自然堆肥14.33、31.31、19.57个百分点。红外光谱变化反映了堆肥过程中木质纤维素、多糖、脂肪和酰胺等成分的减少及芳香结构成分的增加,为菌剂DN-1促进堆肥中有机成分的转化和腐熟进程提供了有力的直接证据。菌剂DN-1具有很好地促进堆肥中木质纤维素降解和提高堆肥腐熟度的潜力,可以将其进一步应用于较大规模的堆肥处理。     

墙体材料及其组合对日光温室墙体保温性能的影响

堆肥是由群落结构演替非常迅速的多个微生物群体共同作用而实现固体废物资源化、无害化的动态过程。本文在综合国内外文献资料的基础上,结合本实验室的研究工作,从堆肥过程中微生物群落的演替、有机物降解菌的选育应用、变性梯度凝胶电泳(DGGE)在堆肥微生物研究中的应用等方面介绍了现代堆肥过程中微生物研究的进展及存在问题,并且指出堆肥过程中微生物菌系组成变化复杂和实验手段有限是限制本研究的主要因素,今后应重视利用分子生物学方法进行微生物的研究工作,并根据微生物之间的协同关系有目的地构建降解多种有机废弃物的高效稳定复合菌系,以适应复杂的堆肥环境。     

Uptake of Hydrocarbon by Pseudomonas fluorescens (P1) and Pseudomonas putida (K1) Strains in the Presence of Surfactants: A Cell Surface Modification

The objective of this research was the evaluation of the effects of exogenous added surfactants on hydrocarbon biodegradation and on cell surface properties. Crude oil hydrocarbons are often difficult to remove from the environment because of their insolubility in water. The addition of surfactants enhances the removal of hydrocarbons by raising the solubility of these compounds. These surfactants cause them to become more vulnerable to degradation, thereby facilitating transportation across the cell membrane. The obtained results showed that the microorganism consortia of bacteria are useful biological agents within environmental bioremediation. The most effective amongst all, as regards biodegradation, were the consortia of Pseudomonas spp. and Bacillus spp. strains. The results indicated that the natural surfactants (rhamnolipides and saponins) are more effective surfactants in hydrocarbon biodegradation as compared to Triton X-100. The addition of natural surfactants enhanced the removal of hydrocarbon and diesel oil from the environment. Very promising was the use of saponins as a surfactant in hydrocarbon biodegradation. This surfactant significantly increases the organic compound biodegradation. In the case of those surfactants that could be easily adsorbed on cells of strains (e.g., rhamnolipides), a change of hydrophobicity to ca. 30-40% was noted. As the final result, an increase in hydrocarbon biodegradation was observed.     

水体生态系统的生物修复研究

生物修复是借助于生物系统降解环境中污染物的有效方法,具有成本低、效率高和有效持续时间长等优点。阐述了水体生物修复进展,重点论述了对水体中烃类污染、水体脱氮以及酶工程和新型反应器在生物修复中的应用。     

Enhanced Biodegradation of Naphthalene and Anthracene by Modified Vermiculite Mixed with Soil

Hydrophobic modified vermiculite mixed with soil was investigated in biodegradation experiments of naphthalene and anthracene. The experiments had been carried out on mixtures of soil and vermiculite at a proportion of 2%, 10%, and 15% and also in the absence of clay used for control. Biodegradation of the pollutants was followed by the decline of naphthalene and anthracene concentration, measured by CG. Compound mineralization was also proved by the evolution of CO₂. The results showed that in the mixture with a higher proportion of vermiculite biodegradation is enhanced compared to that performed in the absence of vermiculite. In general, when vermiculite proportions are increased, the rate of degradation increases, which may account for the bioavailability of compounds. Bioavailability is an important factor for the degradation of compounds with low solubility. Comparison of biodegradation rates shows that naphthalene is degraded faster than anthracene. The chemical structure could be responsible for this observation. However, although we did not identify the microorganism that was in the soil, we can conclude that vermiculite could be an alternative for the bioavailability of such compounds. Vermiculite in the modified form could also be very useful as a barrier to retain organic pollutants in accidental spills.     

UV-TiO2 Photocatalytic Degradation of Landfill Leachate

Mature landfill leachate contains some macromolecular organic substances that are resistant to biodegradation. The photocatalytic process helps to enhance biodegradability of landfill leachate. Batch experiments were employed to determine the optimum conditions for removal of organic matter by UV-TiO₂ photocatalysis. Under optimum conditions, the removal of chemical oxygen demand (COD), dissolved organic carbon (DOC), biological oxygen demand (BOD), and color was determined. Moreover, gas chromatography coupled with mass spectrometry (GC/MS) was used to analyze the organic matter in the treated leachate before and after treatment by the photocatalysis. The experimental results indicated that the removal of COD, DOC, and color by UV-TiO₂ photocatalysis could reach above 60%, 70% and 97%, respectively. Under optimal conditions, the ratio of biological oxygen demand (BOD)/chemical oxygen demand (COD) was elevated from 0.09 to 0.39, representing substantial improvement in biodegradability. GC/MS analysis revealed that 37 out of 72 kinds of organic pollutants in the leachate remained after 72 h treatment. Esters were produced during photocatalytic process and ketones, hydrocarbons, aromatic hydrocarbons, hydroxybenzenes, and acids were easier to be degraded during photocatalytic oxidation processes. The UV-TiO₂ photocatalysis systems proposed may be a cost-effective approach for pre-treatment of landfill leachate.     

Iron compounds and oil biodegradation in overmoistened contaminated soils: A review of publications

In Russia, the areas of oil pollution gradually shift toward the north into the zone of increased moistening with widespread hydromorphic soils. In this zone, the role of the rapid aerobic degradation of hydrocarbons decreases, while that of slow anaerobic degradation increases. The biological reduction of Fe(III) only proceeds at the expense of the energy of oxidation of organic substances, including oil hydrocarbons, in the oil-polluted soils. This favors the development of technogenic gleying. In contrast to the uncontaminated background soils, in which gleying is correctly considered a degradation process, the same process in the oil-contaminated mineral soils plays a positive role, because it is accompanied by the oxidation of organic pollutants, which otherwise penetrate into rivers and lakes with water flows. The role of Fe(III) reduction may be significant: at one of the oil-spill sites, one-third of the organic pollutants degraded within twelve years after an accident in the anaerobic zone due to Fe(III) reduction. Both iron hydroxides and clay minerals enriched in Fe(III) participate in the reduction processes. In the anaerobic zone, the destruction of organic pollutants begins several years after the relevant natural microorganisms become active. The reduction of Fe(III) reaches its maximum faster than the process of methanogenesis. Upon the soil’s cooling in the winter, the reduction of Fe(III) is replaced by the spontaneous formation of iron oxides (oxidogenesis). Thus, alternating reduction ↔ oxidation reactions proceed in the soils with a contrasting temperature regime. Iron oxides formed in the winter are reduced to Fe(II) in the summer and, thus, resume the associated oxidation of organic pollutants upon the stagnant moisture regime. Therefore, upon monitoring of hydromorphic oilcontaminated soils, special attention should be paid to the forms of iron compounds.     

高级氧化技术修复萘污染土壤和地下水研究进展

多环芳烃是土壤和地下水中普遍存在的持久性有机污染物。其中，萘是结构最简单的多环芳烃，具有迁移性强的特点，可通过多种途径在土壤和地下水中富集，是焦化、化工等历史遗留地块重点关注的污染物之一。高级氧化技术高效、安全且经济，因此，基于高级氧化的萘污染土壤和地下水修复技术受到越来越多的关注。本文综述了芬顿和类芬顿氧化、臭氧氧化和过硫酸盐氧化的反应机理，重点阐述了二价铁、微纳级零价铁、铁矿物、铁螯合物等均相及非均相活化剂活化的氧化技术在修复萘污染土壤和地下水方面取得的研究进展，介绍了多种高级氧化技术联合修复以及高级氧化技术与生物降解技术协同修复的研究现状，指出了目前萘的高级氧化技术研究存在的问题，并对研究做出了展望。     

Effect of reduced iron on the degradation of chlorinated hydrocarbons in contaminated soil and ground water: A review of publications

Chlorinated hydrocarbons are among the most hazardous organic pollutants. The traditional remediation technologies, i.e., pumping of contaminated soil- and groundwater and its purification appear to be costly and not very efficient as applied to these pollutants. In the last years, a cheaper method of destroying chlorine-replaced hydrocarbons has been used based on the construction of an artificial permeable barrier, where the process develops with the participation of in situ bacteria activated by zerovalent iron. The forced significant decrease in the redox potential (Eh) down to ?750 mV provides the concentration of electrons necessary for the reduction of chlorinated hydrocarbons. A rise in the pH drastically accelerates the dechlorination process. In addition to chlorine-organic compounds, ground water is often contaminated with heavy metals. The influence of the latter on the effect of zerovalent iron may be different: both accelerating its degradation (Cu) and inhibiting it (Cr). Most of the products of zerovalent iron corrosion, i.e., green rust, magnetite, ferrihydrite, hematite, and goethite, weaken the efficiency of the Fe⁰ barrier by mitigating the dechlorination and complicating the water filtration. However, pyrrhotite FeS, on the contrary, accelerates the dechlorination of chlorine hydrocarbons.     

Properties of root exudates and rhizosphere sediment of Bruguiera gymnorrhiza (L.)

Journal of Soils and Sediments - The rhizosphere plays an important role in promoting the biodegradation and phytoremediation processes of organic pollutants in mangrove sediments; however, the...     

Effect of Composting on Polycyclic Aromatic Hydrocarbons Removal in Sewage Sludge

Changes in the concentrations of 16 polycyclic aromatic hydrocarbons (PAHs) identified by the US Environmental Protection Agency as priority pollutants were investigated during the composting process of sewage sludge mixed with rapeseed marc (9:1, weight base). Results showed that total PAHs concentrations of the sludge sampled in different seasons had far exceeded the accepted Europe Union cut-off limits for land application. Phenanthrene, fluorene and dibenz(a, h) anthracene were dominant PAHs in the sludge, accounting for 62.8~69.6% of the total amount of the 16 PAHs. Composting appeared to be an effective method for the removal of PAHs in sewage sludge. After 50 days of composting, a significant reduction of concentration of the total PAHs was detected as compared with the initial concentration in composting material. The significant relationship between the biodegradation of organic matter and the losses of Σ16 PAHs during composting indicated that microbial degradation was the key process responsible for the efficient removal of PAHs from the sludge. Among all tested PAHs, fluorene was the most recalcitrant and became the primary residual PAH in the composted material. The lower removal rate of fluorene during composting was a limiting factor for the potential land application of the sludge. Further studies are needed to enhance the removal of fluorene in order to achieve a safe utilization of this sludge.     

温度耦合驱动下土壤-地下水有机污染物迁移规律与模拟研究进展

场地土壤-地下水有机污染空间分布受场地温度场、水动力场、化学场和生物场等多场控制。明晰有机污染物在土壤-地下水系统中的空间分布规律和驱动机制，定量模拟污染迁移过程，是有效开展污染控制与修复的前提。在众多的影响因素中，温度通过改变有机污染物的理化性质及多相流、化学/生物作用驱动参数，进而影响其在土水介质中的迁移及空间分布。本文综述了有机污染物理化性质（密度、黏度、溶解度）和有机污染化学/生物驱动（挥发、吸附和生物降解）关键参数与温度之间的解析关系，及考虑温度影响的土壤-地下水中有机污染传质过程模拟的研究进展，并针对目前模拟研究的不足提出了耦合温度场的土壤-地下水有机污染物迁移数学模型，为定量探究温度耦合驱动下的有机污染物迁移转化过程和规律提供启示。