长春城郊蔬菜地土壤中多环芳烃的含量与分布特征

以长春城市郊区菜地土壤为研究对象,采用GC-FID法对该地区土壤中多环芳烃含量进行分析测定,长春城郊菜地土壤中平均含量苯并(a)芘蒽菲萘.该地区土壤中萘,蒽的含量处于尚清洁水平;部分区域土壤中苯并(a)芘和菲的含量处于轻度污染水平.     

新疆准东煤矿开采区域中多环芳烃的污染特征分析

本文采集并分析了新疆准东煤矿开采区域6个采样点的降尘、土壤和植物的样品,对样品中16种多环芳烃(PAHs)的含量进行了分析,结果显示,降尘中∑PAHs在1.07—8.34 mg·kg~(-1)间;土壤中(除1#点位)∑PAHs在0.134—1.06 mg·kg~(-1)间;植物中(除1#点位)∑PAHs在0.163—1.54 mg·kg~(-1)间.降尘中高含量PAHs主要为苯并[b]荧蒽、菲和萘;土壤中高含量PAHs主要为菲、荧蒽和蒽;植物中高含量PAHs主要为萘、菲和芴.降尘、土壤及植物中PAHs均显示出富三环的特征;研究区域土壤中PAHs的苯并(a)芘等效毒性当量结果显示,研究区域土壤中PAHs的污染存在一定的潜在风险.     

邻苯二甲酸二异辛酯致赤子爱胜蚓体细胞氧化损伤的研究

以赤子爱胜蚓为实验材料,探讨了邻苯二甲酸二异辛酯(DEHP)对赤子爱胜蚓(Esisenia foelide)的毒性.DEHP染毒剂量:0、0.2、0.4、0.8、1.6mmol·L-1,染毒2h后采用KCl-SDS沉淀法检测细胞匀浆DNA-蛋白质交联(DPC)系数,硫代巴比妥酸法检测丙二醛(MDA)含量.结果表明:随着DEHP染毒浓度的增加,赤子爱胜蚓细胞匀浆的DPC系数显著升高(F=14.1,p<0.01),并具有剂量-效应关系(r=0.8877,p<0.05),而MDA含量变化不显著,各染毒组与对照组之间不存在显著性差异(F=0.27,p>0.05).以上结果表明,实验浓度的DEHP暴露可使赤子爱胜蚓体细胞发生显著的DNA蛋白质交联,具有遗传毒性.     

上海市某工业区大气颗粒物(PM10)中多环芳烃的来源和分布特征

利用大气采样器采集上海市某工业区焦化厂,电厂和氯碱厂的大气颗粒物(PM10),结果显示,工业区中低环化合物占优势;焦化厂、电厂和氯碱厂含量最高的化合物分别是萘、苊和菲;煤炭燃烧是该工业区焦化厂和电厂多环芳烃的主要来源,氯碱厂多环芳烃可能主要是来自于其上风向的焦化厂,二者可能有弱的相关性;苯并(a)芘含量处于中等污染水平.     

赤子爱胜蚓(Eisenia foetida)对三种土壤Zn、Pb有效态含量的影响

以褐土(Cinnamonsoil)、潮棕壤(Aquicbrownsoil)和酸性棕壤(Acidbrownsoil)为供试土壤,通过培养实验,研究了土壤中重金属Zn、Pb对赤子爱胜蚓(Eiseniafoetida)生长率的影响,赤子爱胜蚓(Eiseniafoetida)对不同土壤中有效态Zn、Pb含量的影响,并与野生环境中生长的灰暗异唇蚓(Allolobaphoracaliginosa)进行比较。结果表明:重金属的污染明显抑制了赤子爱胜蚓的生长;赤子爱胜蚓可以显著提高潮棕壤中DTPA-Pb的含量,对DTPA-Zn的含量影响不大;加赤子爱胜蚓,褐土中DTPA-Zn和Pb的含量显著高于加灰暗异唇蚓,潮棕壤中DTPA-Zn的含量和酸性棕壤中大DTPA-Pb的含量则相反。     

北京地区表层土壤中多环芳烃的分布特征及污染源分析

根据北京地区不同环境功能区62个样品的分析结果,讨论了研究区表层土壤中多环芳烃的分布特征及污染源类型。结果表明：（1）研究区表层土壤中检测到的多环芳烃主要包括萘、苊、菲、惹烯、三芴、荧蒽、芘、、苯并蒽、苯并[b]荧蒽、苯并[k]荧蒽、苯并[e]芘、苯并[a]芘、苝、二苯并[a,h]蒽、茚并[1,2,3–cd]芘、苯并[g,h,i]苝及其同系物;（2）不同环境功能区表层土壤中多环芳烃的组成及质量分数均存在一定的差别,16种优先控制的多环芳烃质量分数为175.1~10 344 ng.g-1,其中城市中心区表层土壤中多环芳烃的质量分数最高,交通干线附近、工矿企业附近表层土壤中PAHs的质量分数较高,林地、果园和农田表层土壤中PAHs的质量分数较低;（3）表层土壤中PAHs既有来源于石油源,也有来源于化石燃料燃烧产物的,但不同功能区二者贡献存在差别,其中农业用地（林地、果园、农田）中PAHs主要来源于石油源（或部分来源于土壤母岩中的有机质）,城区、交通干线附近及工矿企业附近表层土壤中PAHs污染源以化石燃料燃烧产物输入为主。     

土壤Cu、Cd污染对两种蚯蚓种的急性毒性

通过室内模拟重金属Cu、Cd污染实验,测定了在黄泥土条件下赤子爱胜蚓和威廉环毛蚓的急性毒性效应以及体内累积量.结果表明,赤子爱胜蚓体内Cd累积量与土壤Cd浓度呈显著正相关,赤子爱胜蚓和威廉环毛蚓体内Cu累积量在土壤Cu浓度200～392mgkg-1时呈上升趋势,在Cu浓度392～1075.6mgkg-1时呈下降趋势;威廉环毛蚓体内Cd累积量在土壤Cd浓度200～548.8mgkg-1时呈上升趋势,在Cd浓度548.8～1505.8mgkg-1时呈下降趋势.赤子爱胜蚓和威廉环毛蚓的LC50(Cu)分别为387～555mgkg-1和412～653mgkg-1,LC50(Cd)分别为809～1138mgkg-1和708～1030mgkg-1.总体来看,威廉环毛蚓对重金属Cu的累积能力以及耐受性均强于赤子爱胜蚓,而赤子爱胜蚓对Cd的耐受性强于威廉环毛蚓,但累积能力低于威廉环毛蚓.图4表1参25     

中国主要地区表层土壤多环芳烃含量及来源解析

以表层土壤多环芳烃(polycyclic aromatic hydrocarbons,PAHs)为研究对象,查阅2000—2016年间发表的101篇中国主要地区表层土壤多环芳烃的文献,系统分析了中国主要地区表层土壤中PAHs的含量、组分、分布特征及主要来源,为中国土壤多环芳烃污染防治提供科学依据。结果表明:中国主要地区表层土壤中16种优控多环芳烃总量(中位值)(∑PAHs)为515.70 ng·g~(-1),和其他国家相比处于中等水平。16种多环芳烃(PAHs)在表层土中以菲(Phe)、荧蒽(Fla)和萘(Nap)的含量(中位值)最高,苊烯(Acy)、苊(Ane)以及茚苯并(1,2,3,-cd)芘(Inp)含量(中位值)最低;∑PAHs含量(中位值)地域分布表现为西北地区华北地区东北地区华东地区华中地区华南地区西南地区。表层土壤PAHs组成以高环(4环及以上)为主,占60.06%,不同地区PAHs的组成不同;通过对16种检出PAHs进行聚类分析,得出中国主要地区PAHs主要有煤炭燃烧源、油类燃料燃烧源、焦油生产源、石油源和生物质燃烧源等5个来源。结合同分异构体比值法和污染物特征指数法,进一步对22个省区表层土壤PAHs进行聚类分析,得出新疆、天津、陕西表层土壤PAHs主要来源于液化石油燃料及原油的污染,燃料成分主要为汽油;福建、吉林、山西、贵州和江西表层土壤中PAHs主要来源于草、木材、煤炭及生物质燃烧;北京、湖北、黑龙江、安徽、西藏、江苏、广东、浙江、湖南、山东、宁夏、重庆及香港等表层土壤PAHs则主要来源于液体化石燃料、生物质及煤炭的燃烧,燃料成分为煤炭和汽油。     

钢铁工业区周边农业土壤中多环芳烃(PAHs)残留及评价

对某大型矿业企业周边农业土壤中多环芳烃(PAHs)残留量进行了调查。结果表明,PAHs总残留量范围为312. 2~27 580. 9ng·g-1,且以4环以上多环芳烃组分为主。所有土样中均检出PAHs,单一污染物以芘、艹屈、荧蒽、苯并[a]芘、蒽、菲、苯并[a]蒽、苯并[k]荧蒽、茚并[1,2,3 cd]芘、苯并[g,h,i]苝为主。PAHs残留量与有机质含量相关性较好。不同样区土壤PAHs残留量受常年风向影响明显。以加拿大农业区域土壤PAHs的治理标准值为指标,用内梅罗综合指数法进行评价表明,研究区农业土壤达重污染水平的占37%,中度污染的占19%,轻污染的占25%,另有13%的采样点污染程度处于警戒限,仅有6%的采样点尚处于安全级。     

胎盘内多环芳烃分布及源解析研究

探讨多环芳烃在胎盘中的分布,并对其进行源解析。从2012年6月—2013年6月在云南省第一人民医院产科分娩的产妇中随机抽取30例,利用气相色谱-质谱联用仪(GC-MS)检测其胎盘中多环芳烃的含量;比较胎盘的中央部分和边缘部分多环芳烃含量的差异;对多环芳烃进行源解析,探讨其主要来源。胎盘中检测到多种多环芳烃成分;其中2~4个苯环的多环芳烃占总量的90%以上,尤其是萘、苊、芴、菲、蒽、芘、荧蒽的含量较高;萘、苊烯、苊、茚并(1,2,3-c,d)芘、二苯并(a,h)蒽5种多环芳烃在胎盘中央的含量高于边缘,具有显著性差异(P0.05),其他多环芳烃在胎盘中央和边缘的含量无显著性差异(P0.05)。多环芳烃源解析提示80%研究对象体内的多环芳烃主要来自石油产品的燃烧或暴露于石油产品。     

Effects of hydroxypropyl-β-cyclodextrin on pyrene and benzo[α]pyrene: bioavailability and degradation in sotil

Effect of hydroxypropyl-β-cyclodextrin (HPCD) on the bioavailability and biodegradation of the polycyclic aromatic hydrocarbons (PAHs) pyrene (PYR) and benzo[α]pyrene (BaP) in spiked soils was investigated in 14-week incubation experiments. To evaluate the effect of HPCD in soils with a different matrix, humic substance (HS) was added into soil samples. A 6-h Tenax TA extraction method was used to evaluate pollutants bioavailability. The biodegraded and extracted fractions were compared to evaluate the impact of HPCD on PAHs biodegradation. Results indicated positive effects of HPCD on fast desorption behaviours of PAHs. The biodegraded fraction was consistent with that of the extracted for PYR. However, in terms of BaP, the results were contrary which suggests that biological factors may be limiting factors for BaP pollution remediation. HS weakened the HPCD solubilisation effect while accelerated the decay of PYR and BaP, also implying that bioavailability was not the sole factor limiting PAH biodegradation. In addition, analysis of microbial communities demonstrated that HPCD inhibited the growth of some soil bacteria while HS promoted the evolution of some soil microorganisms. A limited population of hydrocarbon degrader populations led to observing incomplete PAH biodegradation even in the presence of HPCD.     

Spatial distribution of PAHs in a contaminated valley in Southeast China

A survey was conducted on the accumulation and spatial distribution of PAHs in surface soils under different land use patterns in a valley in the Yangtze Delta region with an area of 10 km² containing 15 small copper- and zinc-smelting furnaces. Sixty-five topsoil (0–20 cm) samples were collected and 16 PAHs were determined. The average amount of all the 16 PAHs ranged from 0 to 530 μg kg⁻¹ (oven dry basis), with a mean concentration of 33.2 μg kg⁻¹. Benzo[a]pyrene and indeno[1, 2, 3, -cd]pyrene were the two main PAHs present at high concentrations, while pyrene and fluorene had very low concentrations. PAH concentrations were higher in uncultivated than in cultivated soils, and areas of woods and shrubbery had the␣lowest soil PAH contents. The average PAH-homologue concentrations ranked as follows: 5-rings >> 3-rings, 4-rings > 6-rings >2-rings. Much higher concentrations of PAHs were found in the southern part of the sampling area, perhaps due to deposition of airborne particles by the southeasterly winds in winter and spring. We conclude that the small smelting furnaces were the dominant source of PAHs that accumulated in the soils and the southeasterly winds led to the spatial distribution of PAHs in the topsoils. Land vegetation cover and soil utilization patterns also affected the accumulation and distribution of soil PAHs.     

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.     

Reliability of solid phase microextraction in estimating bioavailability of pyrene in soil

Solid phase microextraction (SPME) coupled with gas chromatography was employed to estimate bioavailability of pyrene in soils with different properties of textures, organic matter contents (SOM) and aging periods. Experimental results indicated that biodegradation rates increased from 0.10 (sandy loam) to 0.15 (silty loam) microg g-1 hr1. By contrast, biodegradation rate decreased from 0.10(1.3% SOM) to 0.04 (7.6% SOM) microg g-1hr1. The amounts of pyrene biodegraded decreased 27% when SOM was modified from 1.3 to 7.6%, indicating that distributions of pyrene in soils at biodegradation end points were affected by the SOM. Sequestration as measured by sonication extraction had evidently occurred in aged soil samples. SPME measurements slightly overestimated the amount of pyrene degraded by indigenous and seeded microorganisms, in soils with the different properties (correlation coefficient, R2= 0.74). The present study demonstrates that the SPME method can not replace biodegradation tests commonly used for predicting bioremediation efficacy.     

环毛蚓在高羊茅修复土壤菲污染过程中的作用

为了解土壤动物在植物修复多环芳烃类化合物过程中的作用,采用盆栽试验法,对比研究了蚯蚓（Pheretima sp．）活动对高羊茅（Festuca arundinacea）修复土壤菲污染的影响效应以及各种生物、非生物因子在植物修复菲污染过程中的作用。结果显示,在20．05-322．06mg·kg^-1菲污染水平范围内,与相同污染水平下无蚯蚓作用的菲污染土壤中生长的植株相比,蚯蚓活动促进修复植物高羊茅的生长：试验期间（72d）,修复植物的单株生物量增加9．74％～21．53％,根冠比增加17．26％～21．44％。添加蚯蚓72d后,种植高羊茅的菲污染土壤中,菲的去除率高达61．70％～88．78％,其平均去除率（77．38％）比无蚯蚓活动的土壤-植物系统中的（68．36％）提高了9．02％,比无植物生长的对照组土壤（22．57％）提高54．81％。各种生物（如植物代谢、植物积累、动物积累、微生物降解、植物．微生物交互作用等）、非生物（如渗滤、吸附、光解、挥发等）因子中,植物．微生物交互作用对菲去除的平均贡献率（47．81％）最为突出,比无蚯蚓活动时（42．08％）提高5．73％。说明蚯蚓活动可强化土壤．植物系统对土壤菲污染的修复作用。     

Distribution and vertical migration of polycyclic aromatic hydrocarbons in forest soil pits of southeastern Tibet

PAHs could be transported to Tibetan Plateau in accompany with atmospheric circulation. The forest regions were found be an important sink for PAHs, while their distributions and migrations in forest are still uncertain. In this study, soil profile samples were collected in southeastern Tibet and the concentrations, distributions, and migration of PAHs in forest region were investigated. The PAHs levels in the forest soils were at the low end of remote sites, ranged from 27.4 to 120.3 ng g^?1 on a dry weight based. Due to low ambient temperature and high organic carbon content, enrichment of PAHs was found in higher altitude on north side. According to the soil profiles, the vertical distributions of PAHs in organic layers were mainly influenced by pedogenesis, while the vertical distributions in mineral layers were dominated by downward leaching effect. Enrich factor (EF) of PAHs was estimated, and the values in organic layers were positively correlated with the octanol–air partition coefficients (K _OA), but EFs in mineral layers decreased with the K _OA values. PAHs in the surface soils on the north side of forest were relatively stable, while the migration of PAHs on the south sides and other clearing sites was more active. The leaching rates of PAHs in clearing site ranged between 1.42 and 29.3%. The results from this study are valuable on the characterization of PAHs in Tibetan Plateau.     

Biomarkers indicate mixture toxicities of fluorene and phenanthrene with endosulfan toward earthworm (<Emphasis Type="Italic">Eisenia fetida</Emphasis>)

α-Endosulfan and some polycyclic aromatic compounds (PAHs) are persistent in the environment and can reach crop products via contaminated agricultural soils. They may even be present as mixtures in the soil and induce mixture toxicity in soil organisms such as earthworms. In this study, the combined toxicities of PAHs with α-endosulfan were determined in Eisenia fetida adults using an artificial soil system. α-Endosulfan and five PAHs were tested for their acute toxicity toward E. fetida in artificial soils. Only α-endosulfan, fluorene, and phenanthrene showed acute toxicities, with LC₅₀ values of 9.7, 133.2, and 86.2 mg kg^?1, respectively. A mixture toxicity assay was conducted using α-endosulfan at LC₁₀ and fluorene or phenanthrene at LC₅₀ in the artificial soils. Upon exposure to the mixture of fluorene and α-endosulfan, earthworms were killed in increasing numbers owing to their synergistic effects, while no other mixture showed any additional toxicity toward the earthworms. Along with the acute toxicity results, the biochemical and molecular changes in the fluorene- and phenanthrene-treated earthworms with or without α-endosulfan treatment demonstrated that enhancement of glutathione S-transferase activity was dependent on the addition of PAH chemicals, and the HSP70 gene expression increased with the addition of α-endosulfan. Taken together, these findings contribute toward understanding the adverse effects of pollutants when present separately or in combination with other types of chemicals.     

Removal of high concentrations of polycyclic aromatic hydrocarbons from contaminated soil by biodiesel

Solubilizing experiments were carried out to evaluate the ability of biodiesel to remove polycyclic aromatic hydrocarbons (PAHs) from highly contaminated manufactured gas plant (MGP) and PAHs spiked soils with hydroxypropyl-β-cyclodextrin (HPCD) and tween 80 as comparisons. Biodiesel displayed the highest solubilities of phenanthrene (420.7 mg·L^-1), pyrene (541.0 mg·L^-1), and benzo(a)pyrene (436.3 mg·L^-1). These corresponded to several fold increases relative to 10% HPCD and tween 80. Biodiesel showed a good efficiency for PAH removal from the spiked and MGP soils for both low molecular weight and high molecular weight PAHs at high concentrations. Biodiesel was the best agent for PAH removal from the spiked soils as compared with HPCD and tween 80; as over 77.9% of individual PAH were removed by biodiesel. Tween 80 also showed comparable capability with biodiesel for PAH solubilization at a concentration of 10% for the spiked soils. Biodiesel solubilized a wider range of PAHs as compared to HPCD and tween 80 for the MPG soils. At PAH concentrations of 229.6 and 996.9 mg·kg^-1, biodiesel showed obvious advantage over the 10% HPCD and tween 80, because it removed higher than 80% of total PAH. In this study, a significant difference between PAH removals from the spiked and field MGP soils was observed; PAH removals from the MGP soil by HPCD and tween 80 were much lower than those from the spiked soil. These results demonstrate that the potential for utilizing biodiesel for remediation of highly PAH-contaminated soil has been established.     

玉米修复芘污染土壤的初步研究

采用60d室内盆栽试验,研究了玉米CT38(ZEAMAYSL.)对多环芳烃芘污染土壤的修复作用.结果表明,无论种植玉米土P系列、无植物对照土M系列(无植物且添加叠氮化钠的灭菌土)和对照土W系列(无植物未灭菌土)中芘的可提取浓度都随着时间的推移逐渐减少,种植玉米加快了土壤中可提取态芘浓度的下降.在芘处理浓度为10—100mg.kg-1的污染土壤中,种植玉米CT38的土壤中芘的去除率达81.9%—89.3%,分别比无植物对照土M系列和对照W系列中芘的去除率高67.5%—70.9%和26.2%—47.0%.玉米也可积累少量芘,但积累量所占芘去除量的比例不足0.3%,植物吸收不是芘去除的主要机理.种植玉米增强了土壤中脱氢酶和脲酶等酶活性,从而促进了植物-根圈微生物体系对芘的生物降解.     

PAHs in organic film on glass window surfaces from central Shanghai,China: distribution,sources and risk assessment

Polycyclic aromatic hydrocarbons (PAHs) concentrations were analysed in the organic film on the glass surfaces of different functional areas in central Shanghai. Concentration levels of total PAHs in the organic film ranged from 1,348.5 to 4,007.9 ng m^?2. The concentration of PAHs was lowest in parks and green spaces (1,348.5 ng m^?2) and highest in traffic zones (4,007.9 ng m^?2). A concentration gradient of total PAHs was observed as follows: traffic zones > commercial areas > cultural and educational areas > parks and green spaces. The distribution of PAHs was characterised by 3–4 ring PAHs in the study areas. The most abundant PAHs were phenanthrene (20.5 %), fluorene (16.7 %), pyrene (12.4 %) and chrysene (Chry) (11.2 %). The mass of the bulk film was composed of organic and inorganic compounds and ranged from 246 to 1,288 mg m^?2. The bulk film thickness varied from 144 to 757 nm in the different functional areas. The ratios of An/178 and Fl/202 and principal component analysis suggested that PAHs came mainly from the mixed sources of fossil fuel, coal and incomplete combustion of biomass. Benzo[a]anthracene (BaA)/Chry is not suitable for use as a tracer for the transmission process of PAHs because of the rapid depletion of BaA in the organic film by photooxidation during daylight hours. The concentration of benzo[a]pyrene equivalent (BaPeq) varied from 21 to 701 ng g^?1, and the major carcinogenic contributors of the 16 PAHs were BaP, DahA, B[b/k]F and InP, accounting for 83 % of BaPeq.