混种模式对土壤中PAHs污染的强化修复作用

以菲、芘为多环芳烃(PAHs)的代表,选择多环芳烃初始浓度在20.05~322.06 mg·kg-1的污染土壤为研究对象,采用温室盆栽的方法,选用三叶草(Trifolium repens)单种、紫花苜蓿(Medicago sativa)单种和三叶草-紫花苜蓿混种3种模式,通过测定实验70 d后土壤中PAHs的浓度,研究不同种植模式下植物对PAHs污染的去除效果和修复机制。结果表明,(1)在实验浓度范围内,在三叶草和紫花苜蓿混种模式下,土壤中PAHs的去除率最高,明显高于单种模式。在70 d的实验期间,约有75.47%的菲和68.28%的芘被降解,而单种模式下三叶草和紫花苜蓿对菲的降解率分别为31.79%和64.03%,对芘的降解率分别为27.97%和52.18%。(2)相同污染水平下,茎叶部PAHs的含量低于根部,菲的含量低于芘,混种模式下植物体内PAHs的含量低于单种模式下的含量。(3)生物作用对土壤中菲的去除率在三叶草、紫花苜蓿组和混合组中分别为26.69%、58.98%和69.84%,对芘的去除率分别为25.29%、48.98%和65.86%,明显高于非生物作用。在生物作用中植物-微生物的联合效应是最主要的,在三叶草组、紫花苜蓿组和混合组中对菲、芘的去除率分别为6.95%、34.85%、42.95%和6.3%、26.78%、38.98%。微生物作用在各种模式下相同,混种模式下,植物作用、植物-微生物联合效应均高于单种模式。说明借助多物种混合种植模式对改善PAHs污染土壤修复效果、减少植物体内PAHs积累和缓解生态风险具有可行性。     

蚯蚓驱动的滨海盐碱农田土壤中多环芳烃生物降解的机制研究

滨海盐碱地是中国重要的耕地资源,而人类活动等加重了滨海盐碱地的多环芳烃（PAHs）污染。微生物降解是去除土壤PAHs污染的重要手段。外源微生物的低环境适应性限制了其实际应用,诱导强化土著微生物原位修复具有重要意义。以较难降解的三环芳烃-蒽为多环芳烃代表,湛江市轻度滨海盐碱土为污染研究对象,赤子爱胜蚓（Eisenia foetida）为受试生物,设置4组处理（灭菌对照,SS;灭菌土壤加蚯蚓,SE;自然对照,OS;自然土壤加蚯蚓,OE）。比较不同时间段各处理土壤中蒽的降解效率、理化性质和培养结束时土壤微生物群落结构,明确蚯蚓对粤西地区滨海农田土壤蒽降解的强化效果、降解功能微生物种群和关键环境因子的贡献率。结果表明：蚯蚓能够影响滨海盐碱土壤中蒽的降解,并且加速其降解。在OS中蒽降解率为40.7%,而SS中蒽的降解率仅为17.7%。土壤中蒽的降解以生物降解为主（23.0%）,而不是非生物降解（17.7%）。OE处理的降解效率最高为62.1%,SE处理的降解效率为50.4%。蚯蚓强化非生物降解和肠道菌群作用共同的效果（32.7%）高于蚯蚓强化土著微生物降解的效果（21.4%）。同时,蚯蚓影响了土...     

多环芳烃(PAHs)污染对滨海湿地入侵植物互花米草的影响北大核心CSCD

滨海湿地生态系统正遭受着人为活动或自然因素的威胁,为探究多环芳烃（PAHs）污染对滨海湿地入侵植物互花米草根际、根内微生物的影响及植物-微生物联合修复PAHs的潜力,设置含有不同浓度菲和芘的沉积物处理,通过盆栽实验对互花米草幼苗进行暴露.结果显示,培养70 d后,菲和芘的去除率分别为13%-36%和11%-30%;菲处理的互花米草根际沉积物中脱氢酶活性显著高于对照（P〈0.05）,非根际沉积物多酚氧化酶活性则降低10%.磷脂脂肪酸（PLFA）分析显示,菲处理显著降低了根际沉积物微生物量（P〈0.05）,尤其是革兰氏阴性菌下降了24%;而芘处理对脱氢酶、多酚氧化酶以及总微生物量的影响相对较小.100 mg/kg菲处理使得根际与根内革兰氏阴性菌PAHs-环羟基双加氧酶基因（PAH-RHDα-GN）丰度比对照组分别增加了100倍和3倍;而100 mg/kg芘处理使得根际与非根际沉积物中PAH-RHDα-GP丰度显著升高（P〈0.05）.上述结果表明,入侵植物互花米草对PAHs污染存在明显的响应,其根内细菌在植物-微生物联合修复PAHs污染具有重要的作用.     

污染土壤中菲的修复技术研究进展

菲是多环芳烃中的代表性物质,具有"三致"效应,而且菲的蒸汽压小,辛醇-水分配系数高,生物可利用性低,是一种持久性有机污染物。随着化石燃料的大量使用,受菲污染的土壤越来越多,研究菲的修复技术对污染土壤的再利用具有重要意义。结合目前国内外研究进展,综述了污染土壤中菲的修复方法,包括物理修复、化学修复和生物修复。针对各种修复方法,阐述了其原理、修复条件、实例应用和优缺点,重点论述了植物修复和微生物修复方法的降解机理和应用,分析了微生物性质,包括氧、营养物、温度、土壤理化性质、共存污染物等环境因素对生物降解的影响。由于溶解性的菲有较好的迁移转化能力,因此表面活性剂的助溶作用适用于各种修复方法,选择合适的表面活性剂可以提高修复效果。在各种修复技术中,物理修复是通过物理技术实现菲的解吸与富集,无污染,但是去除率低;化学修复是使用氧化剂将菲氧化分解成无毒易降解的小分子物质或通过添加化学淋洗剂增加菲的溶解性,提高迁移转化能力,用时短,但是引入其他试剂,容易造成二次污染;植物修复是通过植物的提取、降解和固定等过程实现菲的修复,尤其是植物的根际环境为微生物的生长提供有利的条件;微生物修复以菲可作为微生物生长的碳源为基础,在分解酶的作用下实现菲的降解,但是生物修复周期长,可利用的生物少,而且可能生成毒性更高的中间代谢产物。因此,寻找合适的修复物种,采用基因技术提高生物的修复能力或多法联用、取长补短可提高修复效率。最后,在共降解理论的基础上,结合重金属和有机污染物共存时,一种物质的存在对另一种物质的降解有促进作用,提出了协同降解的概念,寻求对多种污染物有协同降解或共降解作用的修复方法是今后发展的主要方向。     

蚯蚓-植物联合修复土壤重金属技术研究:回顾与展望

由于自然和人类活动而产生的重金属污染是目前国内外主要关注的热点问题之一.生态环境部和自然资源部联合发布了一份中国土壤污染现状报告,报告提出中国土壤重金属污染总体形势严峻.蚯蚓-植物联合修复的效果优于单一的植物修复和蚯蚓修复的效果.本文在大量收集文献资料的基础上,回顾了我国的超积累植物研究现状和蚯蚓在植物修复土壤重金属污染的作用.对蚯蚓-植物联合修复优缺点进行归纳,展望了蚯蚓-植物联合修复应用的广阔前景,为蚯蚓-植物联合修复的应用提供参考.针对蚯蚓-植物联合修复技术的应用,指出了今后研究的重点与方向.     

生物修复PAHs污染土壤对酶活性的影响

在PAHs污染土壤生物修复过程中,以黑麦草、苜蓿为修复植物,固定化微生物菌剂为外源微生物,通过盆栽实验研究了不同处理对土壤酶活性的影响,以及酶活性与PAHs的去除效果之间的相关性。结果表明,植物修复、微生物修复及两者联合修复均显著提高了土壤PAHs的去除效果,其中黑麦草和苜蓿与微生物菌剂联合修复效果分别达到37.57%和38.41%,比单独的植物修复和菌剂修复高出一倍左右。各种生物修复同时促进了土壤多酚氧化酶、脱氢酶及脲酶的活性,减少了过氧化氢酶活性。过氧化氢酶活性与多酚氧化酶活性呈显著负相关（P〈0.05）、而脲酶与多酚氧化酶显著正相关（P〈0.05）。进一步分析表明PAHs的去除率与脱氢酶活性极显著正相关（P〈0.01）,与多酚氧化酶活性呈显著正相关（P〈0.05）,与过氧化氢酶活性呈负相关（P=0.564）;因此,在PAHs污染土壤生物修复过程中,可以选择土壤脱氢酶活性和多酚氧化酶活性作为PAHs修复效率的微生态指示指标。     

土壤B[a]P叠加污染对蚯蚓体腔细胞SOD、POD和MDA的毒性效应

采用累积试验方法,研究土壤苯并[a]芘（B[a]P）多次叠加污染对赤子爱胜蚓（Eisenia foetida）体腔细胞超氧化物歧化酶（SOD）、过氧化物酶（POD）和丙二醛（MDA）的毒性效应.结果表明,随着土壤中B[a]P暴露时间的延长,蚯蚓体腔细胞的SOD、POD活力和MDA含量呈初期（1～14 d）下降速率较快,尔后（14～56 d）下降速率减小的变化趋势.在叠加污染条件下,0～ 20 cm深度土壤中蚯蚓体腔细胞SOD活力和MDA含量在14d时分别比一次污染低20.97％和15.96％,POD活力比一次污染高20.44％;而在＞20～40 cm深度土壤中蚯蚓体腔细胞SOD、POD活力和MDA含量在14d时分别比一次污染低52.89％、18.00％和70.60％.表明B[a]P叠加污染土壤中蚯蚓体腔细胞的毒性效应低于一次污染.     

蚯蚓活动对锌污染土壤微生物群落结构及酶活性的影响

以不同质量分数Zn污染高沙土为材料,研究在重金属污染土壤中,蚯蚓活动对土壤微生物数量和各种酶活性的影响。试验结果表明:Zn的加入使土壤蔗糖酶、脲酶活性降低,而对磷酸酶活性没有影响,加Zn量在300mg·kg-1以下时对微生物量碳有促进作用,高于该水平则表现为抑制作用。接种蚯蚓后,土壤细菌和放线菌的群落数明显提高,除各别处理外均达到显著差异,真菌数量没有变化;土壤磷酸酶、蔗糖酶、脲酶等酶活性也因接种蚯蚓而显著提高(p<0.05),随土壤Zn污染质量分数变化,蚯蚓对三种酶活性的影响趋势不同。蚯蚓活动对土壤酶活性的提高一定程度上缓解了重金属对酶的抑制作用。试验结果还表明蚯蚓活动显著提高了各处理土壤的NO3--N含量,相关散点图显示NO3--N含量和植物地上部生物量,地上部Zn质量分数及植物地上部Zn吸收总量间都有明显相关性(r=0.517,r=0.532,r=0.607)。试验初步验证了蚯蚓对Zn污染土壤中微生物和酶活性的改善作用。     

重金属和多环芳烃复合污染对土壤酶活性的影响及定量表征

以土壤脲酶和脱氢酶为探针物质，室内培养条件下较为系统地研究了重金属（Cd、Zn、Pb）和多环芳烃（菲、荧蒽、苯并a芘）复合污染对土壤酶活性的影响及其定量表征、结果表明，复合投加上述污染物能使土壤酶活性受到不同程度的抑制，其中，脱氢酶最为敏感，其活性是表征重金属和多环芳烃复合污染的一项重要的参考指标．对复合污染模型的建立与分析表明，土壤环境中，重金属和多环芳烃复合污染的类型和强度与污染物的浓度和复合污染时间密切相关．影响土壤脲酶活性的主要因子依次为：Cd〉Zn与苯并a芘的交互作用〉Zn〉Pb〉Zn和菲的交互作用，影响土壤脱氢酶活性的主要因子依次为：Cd和Zn的交互作用〉Cd〉Zn〉苯并a芘〉Cd和菲的交互作用，其中，Zn和苯并a芘相互作用对脲酶活性以及Cd和Zn交互作用对脱氢酶活性的影响均表现为拮抗作用，Zn和菲，Cd和菲之间的交互作用，无论是对脲酶还是脱氢酶均表现为协同作用，图1表3参18     

重金属与多环芳烃复合污染土壤的分布特征及修复技术研究进展

土壤中污染物通常以复合污染的形式存在,各种污染物之间的相互作用增加了修复的难度,仅针对单一污染物进行治理通常难以达到土壤修复的要求。该文对重金属与多环芳烃复合污染的分布特征及两者之间的交互作用进行了总结,综述了几种复合污染土壤修复技术(淋洗法、植物修复、微生物修复和电动法)的作用机理及适用条件,并对该类型复合污染土壤修复技术的研究方向提出了展望。     

Dissipation of polycyclic aromatic hydrocarbons and microbial activity in a field soil planted with perennial ryegrass

Dissipation and plant uptake of polycyclic aromatic hydrocarbons (PAHs) in contaminated agricultural soil planted with perennial ryegrass were investigated in a field experiment. After two seasons of grass cultivation the mean concentration of 12 PAHs in soil decreased by 23.4% compared with the initial soil. The 3-, 4-, 5-, and 6-ring PAHs were dissipated by 30.9%, 25.5%, 21.2%, and 16.3% from the soil, respectively. Ryegrass shoots accumulated about 280 μg·kg^-1, shoot dry matter biomass reached 2.48 × 10⁴ kg·ha^-1, and plant uptake accounted for about 0.99% of the decrease in PAHs in the soil. Significantly higher soil enzyme activities and microbial community functional diversity were observed in planted soil than that in the unplanted control. The results suggest that planting ryegrass may promote the dissipation of PAHs in long-term contaminated agricultural soil, and plant-promoted microbial degradation may be a main mechanism of phytoremediation.     

利用三油酸甘油酯-醋酸纤维素复合膜评价土壤中多环芳烃的生物可利用性

将一种新型被动式采样器——三油酸甘油酯-醋酸纤维素复合膜(TECAMs)暴露于10种人工老化土壤中富集萘、菲、芘和苯并[a]芘4种多环芳烃(PAHs),并与土壤模型动物——赤子爱胜蚓(Eiseniafoetida)进行比较以研究该采样器用于评价土壤中多环芳烃生物可利用性的可能性.研究结果表明,TECAMs能有效富集土壤中萘、菲、芘和苯并[a]芘,并在48h内基本达到平衡,远快于赤子爱胜蚓的21d平衡时间.TECAMs内PAHs含量与土壤溶解有机碳(DOC)含量呈正相关(p<0.05),而与土壤中总有机质(TOM)含量呈负相关(p<0.05),土壤pH对TECAMs富集PAHs的影响不显著(p<0.05).TECAMs内PAHs含量与土壤中PAHs含量、赤子爱胜蚓体内PAHs含量均呈显著线性正相关(p<0.05,p<0.01).研究结果表明TECAMs有可能应用于评价土壤中PAHs的生物可利用性.     

热带砖红壤生长的小白菜吸收和累积PAHs的特征

为了了解和掌握热带土壤栽培的小白菜（Brassica rapa L. Chinensis Group.）对多环芳烃（PAHs）污染物的吸收和累积规律,为热带土壤的安全利用及农产品安全生产提供科学依据,于2013 年5-9 月在海南省农垦科学院海口试验站网室内进行了小白菜盆栽试验.各处理土壤分别施加3 种单体 PAHs 的质量分数梯度为0、0.4、0.8、1.6、3.2 mg·kg^-1,撒播小白菜种子出苗后,每盆留苗6 株,自然条件,常规管理,各处理小白菜培养30 d 后收获.小白菜和土壤样品,用超声水浴萃取,层析小柱净化后,利用气相色谱-质谱法测定样品中的3 种PAHs.结果表明,小白菜根和叶中3 种PAHs 累积量随土壤施加质量分数的升高而增加,根部和叶对Phe 最大累积量分别为86.25 ng·g^-1 和37.18 ng·g^-1,而对 BaP 的最大累积量分别为20.78 ng·g^-1 和3.56 ng·g^-1;小白菜根对Phe 与Fla 的生物富集系数较大,且二者无明显差异,但对 BaP 的生物富集系数较小,且差异显著（P=0.006）;3 种PAHs 单体在各种处理土壤中的残留在 84.49%-94.03%之间,各单体之间无明显差异,各处理之间也无明显差异.说明热带土壤生长的小白菜根和叶中3 种单体 PAHs 浓度显著低于其土壤中的浓度,且根部积累3 种单体PAHs 的浓度显著高于其叶中的浓度;小白菜叶对BaP 的吸收和累积量极少;小白菜根更易吸收和累积Phe 和Fla;小白菜生长30 d 后,绝大部分PAHs 仍残留在土壤中.     

Effect of rhizosphere on soil microbial community and pyrene biodegradation

To access the influence of a vegetation on soil microorganisms toward organic pollutant biogegration, this study examined the rhizospheric effects of four plant species (sudan grass, white clover, alfalfa, and fescue) on the soil microbial community and in-situ pyrene (PYR) biodegradation. The results indicated that the spiked PYR levels in soils decreased substantially compared to the control soil without planting. With equal planted densities, the efficiencies of PYR degradation in rhizosphere with sudan grass, white clover, alfalfa and fescue were 34.0%, 28.4%, 27.7%, and 9.9%, respectively. However, on the basis of equal root biomass the efficiencies were in order of white clover >> alfalfa > sudan > fescue. The increased PYR biodegradation was attributed to the enhanced bacterial population and activity induced by plant roots in the rhizosphere. Soil microbial species and biomasses were elucidated in terms of microbial phospholipid ester-linked fatty acid (PLFA) biomarkers. The principal component analysis (PCA) revealed significant changes in PLFA pattern in planted and non-planted soils spiked with PYR. Total PLFAs in planted soils were all higher than those in non-planted soils. PLFA assemblages indicated that bacteria were the primary PYR degrading microorganisms, and that Gram-positive bacteria exhibited higher tolerance to PYR than Gram-negative bacteria did.     

Effect of rhizosphere on soil microbial community and in-situ pyrene biodegradation

To access the influence of a vegetation on soil microorganisms toward organic pollutant biogegration, this study examined the rhizospheric effects of four plant species (sudan grass, white clover, alfalfa, and fescue) on the soil microbial community and in-situ pyrene (PYR) biodegradation. The results indicated that the spiked PYR levels in soils decreased substantially compared to the control soil without planting. With equal planted densities, the efficiencies of PYR degradation in rhizosphere with sudan grass, white clover, alfalfa and fescue were 34.0%, 28.4%, 27.7%, and 9.9%, respectively. However, on the basis of equal root biomass the efficiencies were in order of white clover >> alfalfa > sudan > fescue. The increased PYR biodegradation was attributed to the enhanced bacterial population and activity induced by plant roots in the rhizosphere. Soil microbial species and biomasses were elucidated in terms of microbial phospholipid ester-linked fatty acid (PLFA) biomarkers. The principal component analysis (PCA) revealed significant changes in PLFA pattern in planted and non-planted soils spiked with PYR. Total PLFAs in planted soils were all higher than those in non-planted soils. PLFA assemblages indicated that bacteria were the primary PYR degrading microorganisms, and that Gram-positive bacteria exhibited higher tolerance to PYR than Gram-negative bacteria did.     

Abiotic control on the dissipation of chlorpyrifos spiked in an Udic Ferrisol at a lower dosage

The dissipation routes of chlorpyrifos spiked in an Udic Ferrisol at the dosage of 400 ng g^?1, which represents a residual level after an agricultural application, were studied in a laboratory, using the natural soil under three moisture regimes, sterilised, and organic matter-free soils in the dark at 20°C. The obtained results showed that higher soil moisture caused faster dissipation, and the abiotic and biotic contributions to the total dissipated amount of the applied chlorpyrifos in the soil accounted for 77.3–85.2% and 14.7–22.7%, respectively. In the sterilised soil, the contribution of organic matter to chlorpyrifos dissipation was noticed to account for 95% in the earlier two weeks, and was nearly equal to that of soil minerals two weeks after the incubation.     

Influence of inoculating earthworms on removal of pyrene in soils growing Festuca arundinacea

ABSTRACT

The aim of this study was to examine the potential of inoculating earthworms (Pheretima sp.) in order to enhance phytoremediation of polycyclic aromatic hydrocarbons (PAH) present in soils with the use of tall fescue (Festuca arundinacea). In particular, experiments with or without inoculating earthworms for removal of pyrene was investigated. Results showed that planting of F. arundinacea enhanced the removal of pyrene at initial content over 70 days approximately 54%–80% but only 12%–24% occurred in non-planted soils. After inoculating earthworms, the dissipation rates of pyrene in planted soils were increased up to 61%–86%, which was 6%–12% higher than those in corresponding soils without inoculating earthworms. Among all possible pathways, the contribution of plant--microbial interactions on removal of pyrene was predominant, either with (46%) or without inoculating earthworms (52%), is the primary mechanism of contaminant removal. Data suggest inoculating earthworms may be a feasible way for reinforcing removal of PAH in contaminated sites.     

Plant diversity reduces the effect of multiple heavy metal pollution on soil enzyme activities and microbial community structure

It is unclear whether certain plant species and plant diversity could reduce the impacts of multiple heavy metal pollution on soil microbial structure and soil enzyme activities. Random amplified polymorphic DNA (RAPD) was used to analyze the genetic diversity and microbial similarity in planted and unplanted soil under combined cadmium (Cd) and lead (Pb) pollution. A metal hyperaccumulator, Brassica juncea, and a common plant, Festuca arundinacea Schreb, were used in this research. The results showed that microorganism quantity in planted soil significantly increased, compared with that in unplanted soil with Cd and Pb pollution. The order of microbial community sensitivity in response to Cd and Pb stress was as follows: actinomycetes>bacteria>fungi. Respiration, phosphatase, urease and dehydrogenase activity were significantly inhibited due to Cd and Pb stress. Compared with unplanted soil, planted soils have frequently been reported to have higher rates of microbial activity due to the presence of additional surfaces for microbial colonization and organic compounds released by the plant roots. Two coexisting plants could increase microbe population and the activity of phosphatases, dehydrogenases and, in particular, ureases. Soil enzyme activity was higher in B. juncea phytoremediated soil than in F. arundinacea planted soil in this study. Heavy metal pollution decreased the richness of the soil microbial community, but plant diversity increased DNA sequence diversity and maintained DNA sequence diversity at high levels. The genetic polymorphism under heavy metal stress was higher in B. juncea phytoremediated soil than in F. arundinacea planted soil.     

Concentrations of polycyclic aromatic hydrocarbons in soils of a mangrove forest affected by forest fire

Surface soils affected by forest fires from Igbanko mangrove forest in Nigeria were analyzed for 16 EPA priority polycyclic aromatic hydrocarbons (PAHs) using gas chromatography–mass spectrometry (GC–MS). The total PAHs concentrations in the soils ranged from 63 to 188?µg?kg^?1 dry weight (average: 108?µg?kg^?1). The three predominant PAHs in the soils were naphthalene (Na), fluoranthene (Flu), and benzo(b)fluoranthene (BbF). Compared to the control sample (19?µg?kg^?1), elevated PAHs concentrations were observed in the soils, an indication of some level of PAHs contamination. PAHs source diagnostic ratios of Flu/(Flu?+?Pyr) and Ant/(Ant?+?Phe) indicated that the PAHs have a pyrogenic origin which may have resulted from combustion of grass, wood, or coal. An assessment based on Canadian soil quality guidelines indicated that the studied locations do not pose any serious adverse risk on human health.     

番茄对污染土壤中邻苯二甲酸酯的吸收累积特征

利用盆栽实验研究了番茄对污染土壤中邻苯二甲酸酯(PAEs)的吸收积累特征。结果表明,番茄根系、茎、叶和果实均可以吸收累积PAEs化合物,其含量与土壤污染程度成正相关;相同处理的番茄茎、叶和果实中邻苯二甲酸正丁酯(DBP)含量均高于邻苯二甲酸异辛酯(DEHP),而番茄根系中DBP的含量低于DEHP; 4个不同处理方式土壤中DBP和DEHP的残留量顺序均为:灭菌土壤组灭菌土壤种植番茄苗组未灭菌土壤组未灭菌土壤种植番茄苗组。无论是灭菌处理还是未灭菌处理,有番茄苗组土壤中PAEs含量均低于无番茄苗组,未灭菌土壤种植番茄苗组土壤中PAEs残留量最低,PAEs削减率高达96.39%,有番茄苗组微生物数量大于无番茄苗组。这些说明土壤中PAEs的削减是番茄植物和微生物协同作用的结果。