酸碱调控对泥浆反应去除土壤中多环芳烃的影响研究

采用摇瓶试验模拟研究了酸碱调控对泥浆反应去除污染土壤中多环芳烃的影响,结果表明,泥浆反应对污染土壤中的多环芳烃具有一定的去除效果,长期污染土壤中多环芳烃的去除率为10.6% ~ 20.7%,模拟污染土壤中的去除率为37.4% ~ 42.1%;酸碱调控对不同性质的多环芳烃的去除影响不同,整体上看,酸性条件有利于高环（五环和六环）多环芳烃的去除,而中性条件有利于低环（三环和四环）多环芳烃的去除。在实际修复中,根据污染土壤中多环芳烃的组成进行适当的酸碱调控,可以促进污染土壤的快速修复。     

影响土壤中PAHs降解的环境因素及促进降解的措施

土壤中的多环芳烃(PAHs)类有机污染物的生物有效性低,不易降解。本文综述了影响污染土壤中多环芳烃降解的环境因素和促进降解措施的研究进展。影响土壤中多环芳烃降解的因素,包括水分、养分、土壤物理条件等;促进土壤中多环芳烃降解的措施有:向污染土壤添加有机溶剂、利用冯顿反应、添加堆肥和有机物料等。从目前研究来看,应当通过促进多环芳烃从土壤上解吸和培育具有较高多环芳烃降解能力的微生物来促进多环芳烃污染土壤的修复。     

生物质炭中的污染物含量及其田间施用的环境风险预测

生物质炭在碳固定、污染修复和酸性土壤改良中的应用非常广泛,但对生物质炭中所含污染物的研究甚少,其在田间应用中的环境风险并不清楚。该文选择松针和麦秆为原料,采用不同制备方法,研究了不同条件下获得的生物质炭中的重金属和多环芳烃含量,并初步评估了其田间应用的环境风险。研究表明,不同有机废弃物来源制备的生物质炭中均含有一定量的重金属(0.301～128mg/kg)和多环芳烃(1.48～5.48mg/kg);松针制备的生物质炭中的重金属含量普遍高于麦秆制备的生物质炭,而多环芳烃含量则相反,且高温制备有助于降低生物质炭中的多环芳烃含量;在低施用量的田间条件下,生物质炭的施用不易对土壤造成多环芳烃的环境风险,但在高施用量条件下,生物质炭中含有的多环芳烃容易使土壤中多环芳烃含量达到中度或重度污染的程度;生物质炭中的重金属在土壤中的积累量比较有限,环境风险较小。     

多环芳烃污染土壤表面活性剂清洗及生物柴油强化

针对某焦化厂内高浓度多环芳烃污染土壤,以烷基苷（APG）、十二烷基苯磺酸钠（SDBS）和曲拉通X-100（TX100）为表面活性剂代表物,采用静态平衡法和高效液相色谱分析,探索采用单一及混合表面活性剂清洗修复多环芳烃污染土壤,并考察生物柴油对多环芳烃去除效果的影响。结果表明,单一表面活性剂对土壤中多环芳烃去除率顺序为SDBS〉APG〉TX100。APG／SDBS混合处理及TX100/SDBS为9：1混合处理提高了土壤中多环芳烃去除率,而APG／TX100混合处理没能提高多环芳烃去除率。生物柴油对TX100及TX100／SDBS去除多环芳烃效果没有明显提高,对APG及APG/TX100去除多环芳烃略有提高。当APG／SDBS为9：1时,生物柴油可以使多环芳烃去除率从（63．3±2．0）％提高到（75．6±2．0）％。单一表面活性剂、混合表面活性剂、及表面活性剂-生物柴油乳液对多环芳烃各组分去除率比较类似,对菲的去除率最高,茚并[1,2,3-d]芘次之,其余相对较低。因此,建议采用APG／SDBS＋生物柴油的混合体系对高浓度多环芳烃污染土壤进行修复。     

植物修复多环芳烃污染土壤的根际效应机制研究进展

多环芳烃类有机污染物在土壤中可长期存在,进而通过食物链对人类健康产生重大潜在风险。对多环芳烃污染土壤进行植物修复是一种环境友好且经济有效的污染补救策略。进行植物根际效应机制研究对于开发可持续性多环芳烃污染土壤的植物修复技术具有重要指导意义。对近年来的相关研究工作进行了总结,结果表明:多种禾本科植物具有较强的多环芳烃污染耐受性和较好的修复效能,利用多植物混植的联合修复方式表现出优于单一植物的修复优势。低分子量有机酸类根系分泌物通过与土壤中多环芳烃污染物形成反馈回路决定植物修复体系中多环芳烃的命运。修复植物根系分泌物可塑造特定的根际微生物区系,根际微生物可通过多种机制来降解土壤环境中的多环芳烃。针对在植物修复多环芳烃污染土壤研究过程中尚存在一些问题,提出了未来植物修复根际效应机理研究中应该关注的重点和方向,旨在为优化多环芳烃污染土壤植物修复技术提供科学依据与理论参考。     

苏南某焦化厂场地土壤和地下水特征污染物分布规律研究

以苏南某焦化厂为研究对象,在对污染区域初步识别的基础上,采集了0～4.5 m深的22个土壤样品和2个地下水样品,利用GC/MS等检测了多环芳烃类、总石油烃、苯系物、重金属,总氰化物、挥发酚、硫化物的含量,并研究了其在不同功能区土壤和地下水中的特征分布。结果表明：（1）该焦化场土壤和地下水受到了不同程度的污染,其中炼焦炉周边、焦油和洗油储罐区、焦油和粗苯加工车间是污染最严重的区域;（2）土壤中主要超标污染物是多环芳烃、总氰化物、总石油烃、单环芳香烃、二苯呋喃、苯胺、硫化物、挥发酚和一些苯酚类化合物;（3）地下水重点污染区域粗苯车间受到总氰化物、苯胺、苯酚类、萘、总石油烃、单环芳香烃的严重污染,污水处理站区域地下水主要污染物包括总氰化物、萘、总石油烃、苯。     

皂角苷增强洗脱复合污染土壤中多环芳烃和重金属的作用及机理

通过增溶实验和土壤洗脱实验,研究了一种生物表面活性剂——皂角苷（saponin）对多环芳烃-重金属复合污染土壤的洗脱作用及机理。结果表明,皂角苷对菲、芘等多环芳烃有极强的增溶作用,当皂角苷浓度为0.04%时,菲、芘在液相中的表观溶解度分别增大了约22倍和128倍,因而皂角苷能显著增强多环芳烃污染土壤中菲、芘的洗脱,洗脱效率最大分别可达84.1%和81.4%,增大了约2倍和17倍。皂角苷可与重金属离子形成水溶性的络合物,从而增强洗脱重金属污染土壤中的Zn^2＋和Cd^2＋,在皂角苷浓度为0.4%时,Zn^2＋、Cd^2＋的洗脱效率分别可达93.0%和79.4%,增大了约75倍和8倍。皂角苷可同时洗脱多环芳烃-重金属复合污染土壤中的菲、芘和Zn^2＋、Cd^2＋,洗脱效率分别达87.6%、83.5%和92.3%、78.6%,重金属的存在略增大了皂角苷对菲、芘等多环芳烃的洗脱效率,但多环芳烃对Zn^2＋、Cd^2＋的洗脱效率没有明显影响。皂角苷可同时增强洗脱复合污染土壤中的多环芳烃和重金属,从而为多环芳烃-重金属复合污染土壤的修复奠定基础。     

土壤多环芳烃、重金属及其复合污染的植物修复研究进展

复合污染研究已成为环境科学发展的重要方向之一,重金属和多环芳烃是土壤环境中的重要污染物,开展两者复合污染研究,对于农业环境生态安全具有重要意义。本文结合前人的研究结果,通过分析多环芳烃污染土壤的植物修复和重金属污染土壤的植物修复的研究现状,来探讨植物对重金属和多环芳烃复合污染的修复研究进展,并从生态地理学的角度提出相应的研究趋势,提出植物修复需因地制宜的特性。     

太原小店污灌区农田土壤多环芳烃的污染特征及其来源

[目的]对太原小店污灌区农田土壤多环芳烃(PAHs)的污染特征及来源进行分析,为该区农田土壤环境质量评价及土壤污染防治对策的制定提供科学依据。[方法]采集太原小店污灌区15个表层土壤样品,利用GC/MS分析16种US EPA优控多环芳烃(PAHs)的含量,并对其来源和生态风险进行探讨。[结果]所有样品的16种PAHs均被检出,其检出率为100%。研究区农田土壤中总PAHs的浓度为0.315~7.661μg/g,平均值为3.568μg/g。在组成上,2,3环含量约占总量的64.2%,4环含量约占总量的14.2%,5,6环含量约占总量的21.6%,低环和中环PAHs含量所占的比例较高。根据特征比值法及调查结果判定,农田土壤中PAHs污染来源一方面与灌溉水质及灌溉历史有很大的关系,另一方面,主要通过燃煤或化石燃料产生的PAHs在大气干湿沉降和风力输送作用下进入到土壤环境中。[结论]与国内外其他地区的相关研究比较,小店污灌区农田土壤PAHs含量处于中高等污染水平。依据Maliszewska-Kordybach建议的分级标准评价,该区域所有采样点PAHs总量均超标;但基于我国《土壤环境质量标准(征求意见稿)(GB15618-2008)》提出的16种多PAHs污染物总量的农业用地标准值,该区域均未超出此标准。     

一株副球菌对污染土壤中多环芳烃的降解研究

从受多环芳烃(PAHs)长期污染的土壤中分离到一株降解PAHs的噬氨副球菌(Paracoccus aminovorans)HPD-2.使用HPD-2的菌液对PAHs污染的土壤进行了2周的生物降解试验,结果表明加入HPD-2能够明显提高土壤中PAHs的降解率.加菌土壤中PAHs的总去除率为22.9%,PAHs各组分的降解率在19.5% ～ 36.2% 之间.其中三环PAHs的降解率最高(36.1%),五环次之(26.0%),四环的最低(20.9%).对土壤微生物的计数结果发现,HPD-2的加入显著提高了土壤中细菌的数量,而对放线菌和真菌的影响不明显.PCR-DGGE分析结果表明,降解过程中HPD-2可能成为土壤中的优势菌.以上结果表明该菌株在PAHs污染土壤的生物降解中具有较好的应用前景.     

Comparison of Fenton's Reagent and Ozone Oxidation of Polycyclic Aromatic Hydrocarbons in Aged Contaminated Soils (7 pp)

Background, Aim and Scope   Polycyclic aromatic hydrocarbons (PAHs) are formed as a result of incomplete combustion and are among the most frequently occurring contaminants in soils and sediments. PAHs are of great environmental concern due to their ubiquitous nature and toxicological properties. Consequently, extensive research has been conducted into the development of methods to remediate soils contaminated with PAHs. Fenton's reagent or ozone is the most commonly studied chemical oxidation methods. However, the majority of remediation studies use soils that have been artificially contaminated with either one or a limited number of PAH compounds in the laboratory. Hence, it is essential to extend such studies to soils contaminated with multiple PAHs under field conditions. Objectives   The objective of this study is to investigate the capacity of Fenton's reagent and ozone to degrade PAHs in soils. The soils have been collected from a number of different industrial sites and, therefore, will have been exposed to different PAH compounds in varying concentrations over a range of time periods. The capacity of Fenton's reagent and ozone to degrade PAHs in industrially contaminated soils is compared to results obtained in studies using soils artificially contaminated with PAHs in the laboratory. Materials and Methods: Nine soil samples, contaminated with PAHs, were collected from five different industrial sites in Sweden. For the Fenton's reagent procedure, the pH of the soil slurry samples was adjusted to pH 3 and they were kept at a constant temperature of 70oC whilst H2O2 was added. For the ozone procedure, soil samples were mixed with 50% water and 50% ethanol and kept at a constant temperature of 45 oC. Ozone was then continually introduced to each soil sample over a period of four hours. Following the Fenton's reagent and ozone oxidation procedures, the samples were filtered to isolate the solid phase, which was then extracted using pressurized liquid extraction (PLE). The sample extracts were cleaned up using open columns and then analysed by gas chromatography-mass spectrometry (GC-MS). Results: The relative abundance of the detected PAHs varied between soils, associated with different industries. For example, low molecular weight (LMW) PAHs were more abundant in soil samples collected from wood impregnation sites and high overall PAH degradation efficiencies were observed in soils originating from these sites. In the contaminated soils studied, PAHs were more effectively degraded using Fenton's reagent (PAH degradation efficiency of 40-86%) as opposed to ozone (PAH degradation efficiency of 10-70%). LMW PAHs were more efficiently degraded, using ozone as the oxidizing agent, whereas the use of Fenton's reagent resulted in a more even degradation pattern for PAHs with two through six fused aromatic rings. Discussion: The degradation efficiency for both methods was largely dependent on the initial PAH concentration in the soil sample, with higher degradation observed in highly polluted soils. LMW PAHs are more susceptible to degradation than high molecular weight (HMW) PAHs. As a result of this the relative abundance of large (often carcinogenic) PAHs increased after chemical oxidation treatment, particularly after ozone treatment. Repeated Fenton's reagent treatment did not result in any further degradation of soil PAHs, indicating that residual soil PAHs are strongly sorbed. The effectiveness of the two oxidation treatment approaches differed between industrial sites, thus highlighting the importance of further research into the influence of soil properties on the sorption capacity of PAHs. Conclusions: This study demonstrates that the degree to which chemical oxidation techniques can degrade soil bound PAHs chemical degradation is highly dependent on both the concentration of PAHs in the soils and the compounds present, i.e. the various PAH profiles. Therefore, similarities in the PAH degradation efficiencies in the nine soil samples studied were observed with the two chemical oxidation methods used. However, the degradation performance of Fenton's reagent and ozone differed between the two methods. Overall, Fenton's reagent achieved the highest total PAH degradation due to stronger oxidation conditions. LMW PAHs showed higher susceptibility to oxidation, whereas high molecular weight (HMW) PAHs appear to be strongly sorbed to the soils and therefore less chemically available for oxidation. This study highlights the importance of including soils collected from a range of contaminated sites in remediation studies. Such soil samples will contain PAH contaminants of varying concentrations, chemical and physical properties, and have been aged under field conditions. In addition to the chemical and physical properties of the soils, these factors will all influence the chemical availability of PAHs to oxidation. Recommendations and Perspectives: We recommend including aged contaminated soils in chemical degradation studies. In future chemical remediation work, we intend to investigate the potential influence of the chemical and physical properties of PAHs and soil parameters potential influence on the chemical oxidation efficiency in aged contaminated soils. Due to the vast number of contaminated sites there is a great need of efficient remediation methods throughout the world. This study shows the difficulties which may be experienced when applying remediation methods to a variation of contaminated sites.     

乌鲁木齐市周边地区土壤中多环芳烃的含量及来源

在乌鲁木齐市周边,从乌拉泊到水西沟按不同距离与深度进行土壤样品采集,采用索氏提取法与层析净化法进行预处理,高效液相色谱法测定土壤中16种多环芳烃(PAHs)的含量,并对PAHs进行对比分析、污染评价和来源分析的相关研究。结果表明:总PAHs平均浓度为998.23(306.94~3 652.16)ng/g,污染程度差异不大,处中度污染水平但更接近严重污染水平;16种PAHs的最低检测限为0.20~0.80 ng/g;一些采样点的表层土壤中苯并[a]芘的含量高于土壤质量控制标准。不同层次土壤PAHs的污染程度有所不同,其顺序为表层中层下层;高分子量(4~6环)PAHs占据了总含量的84.1%,低分子量(2~3环)PAHs占据15.9%,得出在乌鲁木齐市周边土壤中PAHs的重要来源是汽车排放,同时煤燃烧排放的贡献也很大。     

多环芳烃污染土壤的植物-微生物联合修复初探

在温室盆栽条件下,通过种植紫花苜蓿单独或联合接种菌根真菌(Glomus caledonium L.)(AM)和多环芳烃专性降解菌(DB),研究了利用植物-微生物强化修复多环芳烃(PAHs)长期污染土壤的效果。试验结果表明,接种菌根真菌和PAHs专性降解菌能促进紫花苜蓿的生长和土壤中PAHs的降解。经过90天修复试验,种植紫花苜蓿接种AM、DB和DB+AM处理的PAHs的降解率分别为47.9%、49.6%、60.1%,均高于只种植紫花苜蓿的对照处理(CK)(21.7%)。另外,随着PAHs苯环数的增加,其平均降解率逐渐降低,但是接种PAHs专性降解菌能够提高4环和5环PAHs的降解率。同时也发现土壤中脱氢酶活性和PAHs降解菌数量越高的处理,土壤PAHs的降解率也越高,这也是种植紫花苜蓿接种微生物能够有效促进土壤PAHs降解的原因。     

Removal of polycyclic aromatic hydrocarbons from soil amended with biosolid or vermicompost in the presence of earthworms (Eisenia fetida)

Earthworms burrow through the soil thereby accumulating many lipophilic organic pollutants from the surrounding environment, so they could be used to remove polycyclic aromatic hydrocarbons (PAHs) from soil. Sterilized and unsterilized soil was contaminated with phenanthrene (Phen), anthracene (Anth) and benzo[a]pyrene (BaP), with or without added Eisenia fetida and biosolid or vermicompost. Concentrations of PAHs were monitored in soil and earthworms for 70 days. Removal of PAHs increased in soil with earthworms added as 91% of Anth, 16% BaP and 99% Phen was dissipated compared to 42%, 3% and 95% in unamended soil. The microorganisms in the gut of the earthworm contributed to PAHs removal and 100% of Phen, 63% of Anth and 58% of BaP was removed from sterilized soil with E. fetida added. Biosolid and to lesser extent vermicompost accelerated removal of PAHs from soil. Applying earthworms to a contaminated site might be an environmentally friendly way to remove hydrocarbons from soil. However, a limitation might be the cost of the large amounts of earthworms required to remove PAHs from soil and the necessity to supply them with sufficient substrate while maintaining the water content of the soil high enough for their normal functioning.     

蚯蚓和丛枝菌根真菌对南瓜修复多环芳烃污染土壤的影响

在温室盆栽实验条件下,研究接种AM(arbuscular mycorrhiza)真菌、蚯蚓(Eisenia fetida)对南瓜(Cucurbita moschata)修复3环以上多环芳烃(PAHs)污染农田土壤的影响,试验设置单接AM真菌、单接蚯蚓、双接AM真菌和蚯蚓、不接种的对照共4个处理,播种10周后收获。结果表明,接种AM真菌和蚯蚓促进AM真菌侵染南瓜,增加南瓜生物量;显著提高南瓜修复土壤中Phe(菲)、An(t蒽)、Py(r芘)、BkF(苯并(k)荧蒽)、BaP(苯并(a)芘)、BPe(r苯并(g,h,i)苝)等PAHs污染物的效率,促进南瓜高效地吸收3~5环PAHs,尤其是AM真菌和蚯蚓共同接种条件下对南瓜修复土壤效果最优;AM真菌利于南瓜转移根系吸收的高浓度PAHs化合物至地上部,降低PAHs对根系的胁迫,增强南瓜在高浓度PAHs污染土壤中存活,有利于南瓜应用于高浓度PAHs污染土壤的高效修复;蚯蚓对南瓜地下部吸持3~5环高分子量的PAHs化合物有积极作用。因此,选用的AM真菌和蚯蚓在土壤中具有协同作用,促进南瓜高效修复PAHs污染土壤。     

Characterization and Sources of PAHs and Potentially Toxic Metals in Urban Environments of Sevilla (Southern Spain)

The purpose of this study was to determine the degree of PAH contamination and the association of PAHs with metals in urban soil samples from Sevilla (Spain). Fifteen polycyclic aromatic hydrocarbons-PAHs (naphthalene, acenaphthene, fluorene, phenanthrene, anthracene, fluoranthene, pyrene, benzo[a]anthracene, chrysene, benzo[b]fluoranthene, benzo[k]fluoranthene, benzo[a]pyrene, dibenzo[a,h]anthracene, benzo[g,h,i]perylene, indeno[1,2,3-c,d]pyrene) and seven metals (Cd, Cr, Cu, Mn, Ni, Pb, Zn) have been evaluated in representative urban soil samples. Forty-one top soils (0–10 cm) under different land use (garden, roadside, riverbank and agricultural allotment) were selected. PAHs from soil samples were extracted by sonication using dichloromethane. The simultaneous quantification of 15 different PAH compounds were carried out by HPLC using multiple wavelength shift in the fluorescence detector. For qualitative analysis a photo diode-array detector was used. Metal (pseudo-total) analysis was carried out by digestion of the soils with aqua regia in microwave oven. The mean concentration of each PAH in urban soils of Sevilla showed a wide range, they are not considered highly contaminated. The results of the sum of 15 PAHs in Sevilla soils are in the range 89.5–4004.2 μg kg^?1, but there seems not to be a correlation between the concentration of PAHs and the land use. Of the 15 PAHs examined, phenanthrene, fluoranthene and pyrene were present at the highest concentrations, being the sum of these PAHs about 40% of the total content. Although metal content were not especially high in most soils, there are significant hints of moderate pollution in some particular spots. Such spots are mainly related with some gardens within the historic quarters of the city. The associations among metals and PAHs content in the soil samples was checked by principal components analysis (PCA). The largest values both for ‘urban’ metals (Pb, Cu and Zn) and for PAHs were mainly found in sites close to the historic quarters of the city in which a heavy traffic of motor vehicles is suffered from years.     

南京有机污染风险区农田土壤多环芳烃污染状况研究

采集南京地区不同有机污染风险区农田表层土壤,用超快速液相色谱仪检测样品中15种EPA优控的多环芳烃(PAHs)含量。结果表明,被检农田土壤多环芳烃总量分布于306.0~1251.3μg kg~(-1)之间,均值682.0μg kg~(-1),四环以上高环多环芳烃占较大比例(80%)。根据欧洲土壤质量标准,所检土壤样本已达污染水平。不同风险污染区农田土壤PAHs的含量由高至低为:钢铁工业区、有机垃圾处理区、化工工业区及炼油工业区。钢铁工业区附近主要的污染物为荧蒽、芘、屈和苯并[a]蒽,分别占到污染物总量的16%、13%、10%和10%。采用荧蒽/(荧蒽+芘)与茚并[1,2,3-cd]芘/(茚并[1,2,3-cd]芘+苯并[g,h,i]苝)比值对各地污染物来源进行分析,结果发现调查区域的PAHs污染物以燃烧源为主,生物质燃料为主要污染物,部分地区同时有石油燃烧污染。     

Enhanced Mobilization of Field Contaminated Soil-bound PAHs to the Aqueous Phase under Anaerobic Conditions

Although microbially-mediated redox environments can alter the characteristics of soil/sediment organic matter (SOM) and its interactions with persistent hydrophobic organic contaminants (HOCs) bound to soils and sediments, the nature of their effects has not been adequately addressed. In this study, a field soil collected from a manufacturer gas plant site and contaminated historically with creosotes was incubated under aerobic and anoxic/anaerobic conditions along with various amendments (extra carbon and enrichment minerals) for stimulating microbial activities. Anaerobic conditions stimulated significant fractions of bound polycyclic aromatic hydrocarbons (PAHs) encompassing naphthalene through benzo[g,h,i]perylene to be mobilized to the aqueous phase, leaving their aqueous phase concentrations far in excess of solubility (increases in their apparent aqueous phase concentrations by factors as high as 62.8 relative to their initial aqueous phase concentrations). Such effects became more evident for high molecular weight PAHs. Dissolved organic matter exhibiting a high affinity for PAHs was liberated from soils during the anaerobic soil incubations. Feasibility of this concept for field applications was evaluated with a lab-scale continuous flow system composed of an anaerobic soil column followed by an aerobic bioreactor inoculated with PAH-degrading microbes. High quantities of PAHs exceeding their aqueous solubilities were eluted from the anaerobic soil column and those mobilized PAHs were readily bioavailable in the secondary aerobic bioreactor. This study may offer a potential method for cost-effective and performance-efficient ex situ remediation technologies (or in situ if appropriate hydrological control available in the contaminated field site) and risk assessment for the HOC-contaminated soils/sediments.     

上海市主要道路绿地土壤中多环芳烃的分布特征

以上海市延安高架、中环和外环3条主要道路的交通繁忙地带绿地土壤为研究对象,调查研究了其多环芳烃(PAHs)的分布状况.结果表明,3条道路绿地土壤中∑16PAHs的含量在538 ～ 2.19×104 μg/kg之间,与国外Maliszewska-Kordybach建立的标准相比,3条道路绿地土壤均受到PAHs的污染,尤其是4 ～ 6环PAHs,其含量占∑16PAHs的90%,分析认为有机质是影响其分布的重要因素之一.3条道路污染程度有所不同,大小顺序为:外环＞延安高架＞中环,这主要与道路建成年限和允许的通车车辆类型有关,通车年限越长,大型卡车越多,土壤所受PAHs污染的程度越严重.