首页 | 本学科首页   官方微博 | 高级检索  
相似文献
 共查询到19条相似文献,搜索用时 139 毫秒
1.
多环芳烃污染土壤的植物-微生物联合修复初探   总被引:4,自引:1,他引:3  
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。  相似文献   

2.
生物表面活性剂强化微生物修复多环芳烃污染土壤的初探   总被引:8,自引:0,他引:8  
刘魏魏  尹睿  林先贵  张晶  陈效民  曾军  汪勇 《土壤学报》2010,47(6):1118-1125
通过温室盆栽实验,单独或联合接种多环芳烃专性降解菌(DB)和添加生物表面活性剂-鼠李糖脂(RH),研究了生物表面活性剂强化微生物修复多环芳烃(PAHs)长期污染土壤的效果。结果表明,添加RH和接种DB能明显促进土壤中PAHs总量和各组分PAHs的降解。经过90 d培养后,添加RH、DB和RH+DB处理的PAHs的降解率分别为21.3%、32.6%、36.0%,较对照分别提高了333.0%、563.3%、633.0%。此外,随着苯环数的增加,土壤中15种PAHs平均降解率逐渐降低。同时也发现DB、RH+DB处理土壤中脱氢酶活性、多酚氧化酶活性和PAHs降解菌数量显著高于CK、RH处理,但是CK与RH处理没有显著差异,说明DB、RH在促进土壤中PAHs的降解方面有不同的机制。  相似文献   

3.
研究了种植紫花苜蓿 (MedicagosativaL )在接种和不接种菌根真菌 (GlomuscaledoniumL )情况下对土壤中苯并 [a]芘 (B[a]P)的降解动态。历经 90天的温室盆栽试验表明 ,较高浓度 (10 0mgkg-1)B[a]P能降低菌根真菌对植物根的侵染率。种植紫花苜蓿和接种菌根真菌能促进土壤中可提取态B[a]P的降解 ,在接种情况下 ,有植物时对三种浓度 (1mgkg-1,10mgkg-1,10 0mgkg-1)B[a]P的降解率分别达 86 2 %、86 6 %、5 7 0 % ;而没有植物时B[a]P的降解率为 5 3 5 %、5 3 0 %、33 0 %。不接菌根真菌时的降解率比接菌根真菌的低得多 ,不接种菌根真菌时 ,有植物的B[a]P降解率分别达 75 9%、77 7%、5 3 4 % ;而不种植物的降解率分别为 5 4 9%、5 2 6 %、34 1% ,低、中浓度 (1mgkg-1,10mgkg-1)两处理的降解率明显地高于高浓度处理(p <0 0 5 )。B[a]P添加对土壤中多酚氧化酶活性有较大的影响 ,特别是高浓度B[a]P处理土壤的酶活性明显地低于其它三个处理 ,接种菌根真菌能够提高土壤中的酶活性 ,从而促进了土壤中B[a]P的降解。  相似文献   

4.
一株副球菌对污染土壤中多环芳烃的降解研究   总被引:5,自引:1,他引:4  
毛健  骆永明  滕应  李振高 《土壤》2009,41(3):448-453
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.  相似文献   

5.
针对城郊农田土壤中多环芳烃和抗生素复合污染的新特征,通过室内模拟土培实验,研究四环素(Tetracycline,TC)胁迫下,降解菌Sphingobium sp.PHE3对长三角典型农田土壤中芘的降解效果和影响机制。研究表明,接种降解菌处理(B)能明显促进土壤中芘的降解,TC的引入可显著抑制土壤中芘的深度降解过程(P0.05)。经过90天培养后,B处理与接菌+添加TC处理(BTC)的降解率分别为40.1%、25.7%,较对照分别提高了23.0倍、14.1倍。通过土壤微生物群落结构多样性分析发现,降解菌数量在经历90天的土壤环境适应期后逐渐快速增加,其数量变化与污染物芘在土壤中含量消减趋势呈负相关;引入芘和四环素对土壤细菌群落结构多样性和功能稳定性具有显著影响(P0.05),然而对土壤真菌群落影响不显著(P0.05)。此外,B和BTC处理条件下,土壤过氧化氢酶活性、荧光素二乙酸酯酶活性和土壤微生物生物量碳氮值显著高于单独添加芘处理(P)和单独添加TC处理(TC),但P处理与TC处理之间无显著差异(P0.05),说明外源污染物(芘或四环素)对于土壤酶活性和微生物生物量碳氮具有显著抑制作用(P0.05),致使降解菌功能作用受到抑制。综上研究结果表明TC可明显抑制土壤中典型四环多环芳烃的微生物降解过程,针对多环芳烃与抗生素复合有机污染农田土壤的微生物强化修复技术有待深入研究。  相似文献   

6.
PAHs生物降解程度受多种因素影响。通过筛选驯化PAHs降解菌,研究混合菌对土壤中菲、芘、苯并(a)蒽、苯并(b)荧蒽、苯并(k)荧蒽、茚并(1,2,3-cd)芘的生物降解性能,并考察污染时间对土壤中PAHs降解效果的影响。结果表明,筛选的混合菌具有很强的PAHs降解能力,缩短了PAHs生物降解的半衰期,且PAHs起始降解速率较快,之后趋于平缓。27d内土壤中的菲、芘、苯并(a)蒽、苯并(b)荧蒽、苯并(k)荧蒽、茚并(1,2,3-cd)芘的平均降解率分别为98.14%、89.97%、88.47%、63.55%、65.24%、60.49%,其中菲在5d之内的降解率高于93%。污染210d的土壤中各PAHs的起始降解速率高于污染50d的土壤,因此污染时间越长,PAHs生物降解的停滞期越短。  相似文献   

7.
多环芳烃高效降解菌的筛选   总被引:2,自引:1,他引:1  
以多环芳烃(PAHs)菲、蒽、芘、■和苯并(a)芘为供试物,对土著混合菌和引进菌同时进行筛选实验。结果表明,引进菌和土著混合菌经过驯化后对菲、蒽、芘、■和苯并(a)芘均具有一定的降解能力。其中,在pH=6时,混合菌U03在48h内对5种PAHs的降解率均相对较高,分别为:72.38%;64.46%;65.77%;66.49%和64.77%,并且其的降解速率在各菌剂中同样最快,通过SPSS数理统计分析软件对数据进行处理后得出,混合菌U03可在较短时间内达到较好的降解目的。室内模拟试验证明混合菌U03具有较强的降解PAHs的能力,混合菌的协同作用有利于污染土壤中PAHs的降解。  相似文献   

8.
采用温室盆栽试验,以无芒雀麦(W)为修复植物,研究淀粉(D)不同剂量与无芒雀麦组合对煤矿区多环芳烃(PAHs)长期污染农田土壤修复的影响。结果表明,在土壤中添加淀粉剂量D1、D2培养3个月后,显著促进了土著微生物对煤矿区长期污染农田土壤PAHs的降解。D1、D2处理土壤中16种PAHs总量降解率(16.82%,19.06%)分别比对照CK(11.12%)提高了51.26%和71.40%,尤其对6环PAHs的降解增效最为突出。D2处理对6环PAHs的降解达最高,为37.05%,比CK处理提高了241.01%,且为D1处理的1.77倍。在污染土壤中添加淀粉并种植无芒雀麦(D1+W,D2+W)后,与对照CK、淀粉(D)和种植无芒雀麦单一处理(W)相比,土壤中16种PAHs总量降解率有了明显增加,D1+W与D2+W处理下16种PAHs降解率分别为26.26%和28.39%;在PAHs不同环数中对5,6环PAHs的修复效果提升最为明显,对其它环数PAHs降解效果提升不显著,其中5环和6环PAHs降解率在D2+W组合处理下达到最高,为48.63%和58.32%,比CK处理提高了110.36%和436.82%,比无芒雀麦单一处理提高了27.50%和47.77%。从土壤酶活性角度,淀粉、无芒雀麦单一处理及其组合下的土壤过氧化氢酶活性差异不明显,但均显著高于对照CK处理;无芒雀麦对多酚氧化酶活性有明显的激活作用,且与淀粉组合进一步显著提升了该酶的活性,与D1+W与D2+W组合下的5,6环PAHs降解率达最高相一致。综上,利用淀粉与无芒雀麦的优化组合形式能明显提升煤矿区5,6环PAHs长期污染农田土壤的修复效果,可以作为该区污染土壤修复治理的一种选择。  相似文献   

9.
多环芳烃微生物降解机理研究进展   总被引:1,自引:0,他引:1  
唐婷婷  金卫根 《土壤》2010,42(6):876-881
主要阐述了微生物降解PAHs的机理,比较了典型微生物种类芽孢杆菌(Bacillus)和分支杆菌(M.vanbaalenii PYR-1)对同种PAHs菲的代谢过程不同之处,并分析了分支杆菌(M.vanbaalenii PYR-1)对菲和芘的代谢机理,指出微生物氧化降解PAHs主要从其K区和湾区开始,而K区氧化是有毒PAHs降解的主要可能途径,资料显示真菌比细菌对苯并[a]芘的降解能力更强,同时给出了微生物代谢菲、芘和苯并[a]芘的降解图,以便做进一步研究。  相似文献   

10.
在恒温和恒定转速培养条件下,模拟生物泥浆反应器法,选择从石油污染土壤中分离出来的青霉菌、黑曲霉、白腐真菌等3种真菌,在添加不同浓度菲和邻苯二甲酸作为共存底物情况下,研究其对水稻土中苯并[a]芘(B[a]P)的共代谢降解。结果表明,未灭菌土壤对B[a]P有降解能力。当土壤中添加菲时,提高了B[a]P在土壤中的降解率,100 mg kg-1浓度菲处理的降解率显著高于200 mg kg-1浓度菲处理,邻苯二甲酸对B[a]P降解影响不大。灭菌土壤中的B[a]P几乎没有降解。添加菲及邻苯二甲酸均促进了青霉菌对B[a]P的降解,其中菲浓度为100 mg kg-1处理效果最显著。与灭菌土壤相比,接种黑曲霉提高了B[a]P的降解率,但添加菲与邻苯二甲酸却均抑制了黑曲霉菌对B[a]P的降解。白腐真菌能有效地降解B[a]P,但高浓度菲抑制了白腐真菌对B[a]P的降解,同时邻苯二甲酸对促进白腐真菌降解B[a]P的效果不明显。  相似文献   

11.
多氯联苯复合污染土壤的土著微生物修复强化措施研究   总被引:11,自引:1,他引:10  
滕应  骆永明  李振高  邹德勋 《土壤》2006,38(5):645-651
通过室内模拟试验,以不同C源、C/N比、水分及通透性为调控因子,对多氯联苯(PCBs)长期复合污染土壤的土著微生物强化修复进行了初步研究。结果表明,PCBs长期复合污染土壤中,在土壤水分含量为田间持水量的60%时,加入淀粉、葡萄糖和琥珀酸钠均在一定程度上增加了细菌和真菌数量,从而促进土壤中PCBs的土著微生物降解。不同种类的C源对PCBs污染土壤的土著微生物降解效果存在明显差异,且其降解效果与C源的施用剂量密切相关。当淀粉加入量为C1.0g/kg土时,土壤中PCBs的降解效果较好,而葡萄糖和琥珀酸钠加入量为C0.2g/kg土时,PCBs的降解效果明显。土壤C/N比为10:1的处理效果优于C/N比为25:1和40:1。土壤人为翻动有利于PCBs污染土壤中细菌和真菌的生长,提高土著微生物的代谢活性,从而促进土壤中PCBs的自然降解。这为进一步探讨加速土壤中PCBs降解的最适条件和研发POPs污染土壤的生物修复技术提供了科学依据。  相似文献   

12.
李力  陈明茹  张久红  张军  黄应平  袁喜  李萌 《土壤》2022,54(5):1058-1063
本文通过土壤腐解试验研究外源添加水稻或玉米秸秆对多环芳烃(PAHs)污染土壤CO2-C释放和污染物去除率的影响,同时清晰秸秆腐解中间产物溶解性有机碳(DOC)与土壤PAHs降解的关系。结果表明:秸秆添加处理促进了PAHs污染土壤CO2-C的释放,以玉米秸秆提升效果较好。外源添加秸秆显著增加了土壤DOC含量,且增加幅度随秸秆添加量的增加而增大;水稻秸秆对土壤DOC含量的提升幅度较大。与对照相比,秸秆添加处理下土壤菲、芘残留量均显著降低,菲、芘去除率显著增加,去除效果:玉米>水稻,高量>低量,菲>芘;与对照相比,添加高量玉米秸秆处理(PY15)对土壤菲、芘去除率的增加幅度分别为91.7%和182%。此外,在一定范围内土壤DOC含量与PAHs去除率呈正相关关系。可见,农作物秸秆,尤其是玉米秸秆添加可提升PAHs污染土壤有机碳矿化,亦可在提升土壤DOC含量的同时促进污染土壤PAHs的降解。  相似文献   

13.
为研究外源铀对土壤微生态的影响,设置不同浓度(0、10、20、50、100、150 mg·kg-1)的铀对土壤进行处理,测定各铀处理组中土壤酶活性和微生物功能多样性。Biolog-ECO微平板技术分析结果表明,随着铀污染浓度升高,微生物活性逐渐降低;各铀处理组土壤微生物群落Shannon、Simpson、McIntosh多样性指数均显著低于对照组。铀处理后,六大类碳源利用能力较对照组显著降低,其中酚酸类碳源平均颜色变化率(AWCD)仅为对照组的19.98%。对照组中,微生物对胺类碳源利用能力最高;10 mg·kg-1铀处理组中,微生物对多聚物类碳源利用能力最高;50、100和150 mg·kg-1铀处理组中,微生物对羧酸类碳源利用能力最高。酶活性分析表明,随着铀污染浓度升高,碱性磷酸酶和芳基硫酸酯酶活性均呈下降趋势,而亚硝酸还原酶活性呈先升高后降低的趋势。纤维素酶活性仅在高浓度铀污染土壤中受到抑制。铀处理第30天,酶活性受到的抑制作用最强。4种酶对铀敏感程度依次为芳基硫酸酯酶>碱性磷酸酶>亚硝酸还原酶>纤维素酶。综上可知,铀污染对土壤微生物群落碳源利用能力有显著的抑制作用,同时芳基硫酸酯酶可有效表征土壤受铀污染程度。本研究结果为评估和修复铀污染生态环境提供了理论依据。  相似文献   

14.
以菲和芘为多环芳烃(PAHs)代表物,以紫花苜蓿(Medicago sativa L.)为宿主植物,选用幼套球囊霉(Glomus etunicatum, Ge)、摩西球囊霉(Glomus mosseae,Gm)和层状球囊霉(Glomus lamellosum,Gla)3种丛枝菌根真菌(AMF),研究了接种AMF下土壤中AMF菌丝密度、球囊霉素含量与PAHs去除率的关系。35~75 d,接种Ge、Gm、Gla处理的土壤中菌丝密度、总球囊霉素含量、易提取球囊霉素含量均随时间延长而显著增大,与不接种对照相比,75 d时接种Ge、Gm、Gla处理的土壤中易提取球囊霉素含量提高了48.58%、55.99%和50.23%,总球囊霉素含量则提高了38.75%、50.95%和46.12%。接种AMF促进了土壤中菲和芘的去除,随着时间(35~75 d)延长,接种Ge、Gm、Gla处理的土壤中菲去除率分别高达83.4%~92.7%、82.1%~93.8%、86.9%~93.4%,芘去除率达42.2%~63.5%、43.7%~69.2%、44.6%~66.4%。接种Ge、Gm和Gla处理土壤中AMF菌丝密度、总球囊霉素含量均与土壤中菲和芘的去除率之间存在极显著正相关关系,表明接种AMF提高了土壤中AMF菌丝密度和总球囊霉素含量,并促进了土壤中PAHs的去除。研究结果为阐明丛枝菌根修复PAHs污染土壤的规律及机理提供了依据。  相似文献   

15.
采用盆栽试验法,研究了苏丹草对土壤中菲、芘的去除效果,及植物和微生物在去除土壤菲、芘中的交互效应。结果显示,在试验浓度范围(0-322.06mg·kg^-1内,土壤~苏丹草系统(TR,)对菲、芘的去除效果明显。种植苏丹草60d后,土壤菲、芘去除率分别为73.07%-83.92%、63%~77.62%;平均去除率分别比对照1(无植物,不加0.1%NaN3)高55.58%、50.71%,比对照2(无植物,加0.1%NaN3)高72.71%、66.57%,说明种植苏丹草可以促进微生物对土壤中芘、菲降解。土壤酶活性测定结果也显示,酶活性越高,污染物降解率越高,反之亦然。因此,植物一微生物间的交互效应是土壤中多环芳烃降解的主要途径。  相似文献   

16.

Purpose

The assessing bias of rhizosphere effect on polycyclic aromatic hydrocarbons (PAHs) degradation in soils would come out from formation of nonextractable PAHs and extractability difference of various solvents. The aim of this study was to evaluate the role of rhizosphere effect in long-term PAHs polluted soils by using sequential extraction approach.

Material and methods

The scheme of sequential extraction included methanol/water extractable PAHs, butanol extractable PAHs, DCM extractable PAHs, humic acid-bound PAHs, crude humin-bound PAHs, and organic-C enriched humin-bound PAHs. PAHs in plant tissues were extracted by dichloromethane after saponifying. The correlations between PAHs in plant tissues and sequentially extracted fractions were generated by partial least squares regression.

Results and discussion

The profiles of sequentially extracted PAHs varied with plant species. The discrepancy of toxicity equivalency concentrations between rhizosphere and bulk soils was much more significant than that of total PAHs concentrations. In partial least squares regression models, the concentration of PAHs in plant tissues was correlated with fractions strongly associated with soil.

Conclusions

The novelty of this study is the evaluation of concentration and toxicity equivalency concentration of PAHs in rhizosphere of crops sampled in a field polluted with PAHs for long term. This study has highlighted more significant role of rhizosphere in cleanup of cancerogenic toxicity of soil than amount of PAHs in polluted soils.  相似文献   

17.
多环芳烃(PAHs)在土壤不同活性有机质库中的分配会影响它们在土壤中的迁移和生物有效性。本研究采用土壤有机无机复合体的分组方法,分离出以游离态有机物质存在的轻组和以有机无机复合体存在的重组,研究了15种美国环境保护署(USEPA)优控的PAHs在土壤轻组和重组以及重组结合态腐殖质不同组分中的分配特征。结果表明,轻组中PAHs总量的含量范围为1.30×104~1.07×105μg kg-1,远远高于PAHs总量的含量为221.7~297.8μg kg-1的重组。土壤中轻组的含量虽然只有0.4%~2.3%,但它结合的PAHs量却占土壤中PAHs总量的31.5%~69.5%。重组中PAHs含量主要分布在紧结态腐殖质中,占重组PAHs总量71.2%~87.2%。结合态腐殖质不同组分中PAHs的含量与它们有机碳的含量呈显著性正相关(p<0.01),紧结态腐殖质对PAHs的富集能力显著高于稳结态和松结态腐殖质。PAHs污染土壤的环境风险可能主要在于轻组结合的PAHs。  相似文献   

18.
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.  相似文献   

19.
粉煤灰堆场附近农田土壤硒环境污染评价   总被引:3,自引:1,他引:2  
对贞观山煤灰库附近农田土壤、土壤剖面、灌溉水、母岩以及稻米,蔬菜等农作物中Se含量特征及污染现状进行了系统分析与评价.结果显示:煤灰库周围的农田土壤Se含量范围为0.15~6.12mg/kg,受到不同程度污染.土壤Se含量空间分布特征表明.离煤灰库越近的农田土壤Se污染越严重.农田土壤Se污染主要是由Se含量超标地表水灌溉以及煤灰库的长期处置所引起的,受母岩的影响不大.研究区稻米Se含量较高,为0.04~1.12mg/kg,部分稻米样品Se含量超标严重,并且受土壤Se污染影响明显.长期食用Se含量超标大米对人体健康会产生潜在危害.  相似文献   

设为首页 | 免责声明 | 关于勤云 | 加入收藏

Copyright©北京勤云科技发展有限公司  京ICP备09084417号