天堂国产午夜亚洲专区-少妇人妻综合久久蜜臀-国产成人户外露出视频在线-国产91传媒一区二区三区

當前位置:主頁 > 碩博論文 > 工程博士論文 >

苯胺降解菌在含水層中的遷移機制及污染修復效能研究

發(fā)布時間:2018-03-09 10:17

  本文選題:地下水污染 切入點:生物強化 出處:《吉林大學》2017年博士論文 論文類型:學位論文


【摘要】:隨著城市化和社會經濟的高速發(fā)展,污染物的泄漏導致地下水的嚴重污染,特別是有機污染普遍存在,對人類飲用水安全構成了嚴重的威脅。苯胺是現代農業(yè)、醫(yī)藥和化工產品的常用原料,應用范圍非常廣泛,對地下水的污染比較普遍。由于苯胺對人體具有毒性、致癌、致突變性和在環(huán)境中的持久性,苯胺污染地下水的防治受到了人們的普遍關注。在苯胺污染地下水修復方法中,物理修復技術能耗及處理成本高,化學修復技術則易對環(huán)境造成二次污染,而原位生物修復技術由于其相對經濟、有效和環(huán)境友好且易和多種修復手段聯合應用等特點,具有明顯優(yōu)勢。其中,生物強化可通過向地下環(huán)境中注入外源降解菌,達到縮短修復時間、提高修復效率的目的。但是,實際修復中往往由于外源降解菌在投加到場地后活性和數量大幅度降低,導致生物強化失敗。所以,外源降解菌在地下環(huán)境中的存活和遷移對生物強化至關重要。本論文通過研究含水層中的降解菌存活、降解菌遷移和生物強化修復效率三者之間的關系,為實際生物強化原位修復苯胺污染地下水提供理論基礎。通過之前的研究表明,Pseudomonas migulae AN-1是一株適冷、高效的苯胺降解菌,其在低溫下的降解性能已經清楚,降解條件也被優(yōu)化,但AN-1在地下環(huán)境中的存活、遷移和對苯胺污染含水層的修復效能尚未明確。本論文研究了AN-1在含水層中存活和遷移的相關性能;構建了一種新的綠色熒光蛋白(Green fluorescent protein,GFP)標記結合光投射技術的方法體系,直觀并實時監(jiān)測了降解菌在模擬含水層中的遷移,首次實現了無擾動同時捕捉游離菌和附著菌的遷移動態(tài),揭示了降解菌在含水層中的遷移機制,對明確修復范圍及強化調控生物修復具有重要的指導意義;運用皂素對降解菌在含水層中的遷移進行強化,通過研究AN-1—液體—固體介質三者的表面熱力學性質、界面表面能、吉布斯自由能和DLVO相互作用能,進一步闡明了皂素強化遷移的機理,為強化生物修復和緩解生物堵塞在理論和技術上奠定了基礎;考察并驗證了AN-1在模擬苯胺污染含水層中的存活、遷移和修復效能,建立了一套較為完整的原位生物修復苯胺污染地下水技術體系,對實際修復具有重要參考價值。通過上述研究,本論文主要得出以下結論:⑴AN-1在含水層中存活和遷移的相關特性AN-1可適應苯胺濃度的變化,自動調節(jié)自身的細胞膜通透性、疏水性和自聚集性。AN-1具有附著成膜能力,且AN-1形成的生物膜也具有較好的苯胺降解及抗苯胺沖擊性能。地下水中的Ca2+和SO42-(≥5 m M)對AN-1成膜有促進作用,Fe2+有抑制作用。⑵AN-1在含水層中的遷移機制采用GFP標記結合光透射技術,無擾動同時捕捉了模擬含水層中游離菌和附著菌的遷移動態(tài),直觀并定量的揭示了AN-1在含水層中的遷移機制,即降解菌在含水層中的遷移受自身生物特性和地下水對流、彌散的共同作用,為生物因素和水文地質因素共同影響。(1)降解菌遷移速度:AN-1遷移速度比地下水流速快,且含水層介質粒徑越小,對AN-1遷移速度促進越大,AN-1遷移越快。(2)降解菌遷移能力:含水層介質粒徑越大、地下水流速越快、地下水中離子強度越小、溶解性有機質越多,AN-1在飽和多孔介質中的質量回收率就越大,沉積速率系數越小,越易在含水層中遷移。其中,相同離子強度、相同陰離子,二價陽離子比一價陽離子對AN-1遷移的抑制作用大;相同離子強度、相同陽離子,二價陰離子比一價陰離子對AN-1遷移的抑制作用小。(3)降解菌遷移動態(tài):對于菌羽的初始形狀,菌羽在中砂中沿注入井形成一條窄帶,在粗砂中于注入井下半部形成一個橢球;對于菌羽的面積,與時間呈線性關系,而且在相同降解菌注入量、相同時間內、相同地下水流速條件下,中砂中的面積大于粗砂;對于菌羽的范圍,從注入井至降解菌羽鋒面,可形成連續(xù)的微生物帶,包括游離菌羽區(qū)域和后方的附著菌區(qū)域,對明確修復范圍及強化調控生物修復具有重要的指導意義。⑶AN-1在含水層中遷移的強化皂素對AN-1無毒害作用。當0.1%、0.3%或0.5%皂素存在時,AN-1對苯胺的降解速率比無皂素時略高,生物量略大。確立了0.1%為皂素沖洗溶液的最佳濃度,該濃度下AN-1—液體—固體介質三者構成體系的界面表面能最小、吉布斯自由能最大、細菌截留量最小。采用0.1%皂素溶液沖洗的方法(不用皂素對AN-1進行預處理,直接注入含水層,再用0.1%皂素溶液進行沖洗),是強化AN-1在含水層中遷移最經濟、最有效的方式。該技術方法可使AN-1在含水層中發(fā)生有效的二次遷移,進一步擴大潛在的生物強化修復范圍。離子不影響皂素對AN-1的促遷移作用。當皂素與離子共存時,與離子單獨存在相比,皂素顯著提高了AN-1與介質顆粒之間的能量壁壘,基本消除了離子對AN-1遷移的抑制作用,促進了AN-1在飽和多孔介質中的遷移。⑷AN-1修復模擬苯胺污染含水層在模擬苯胺污染含水層中,AN-1能夠較好的存活,表現出良好的降解性能,并可維護土著微生物群落結構,使種群適應苯胺的沖擊。從注入井至降解菌羽鋒面,可形成連續(xù)的微生物反應帶,有效的修復范圍包括游離菌羽區(qū)域和后方的降解菌附著區(qū)域。當降解菌在污染含水層中注入時,降解菌會大量附著生長并聚集在注入井的附近,雖然該區(qū)域對苯胺的降解速率較大,為主要降解區(qū)域,但可能會形成潛在的生物堵塞。降解菌聚集區(qū)域會隨水流緩慢向下游運移、擴大,并伴隨游離細胞的不斷剝落、隨水流向下游遷移。AN-1對模擬苯胺污染含水層具有良好的生物強化修復效能。本論文的主要創(chuàng)新體現在:構建了一種新的GFP標記結合光投射技術的方法體系,直觀并實時監(jiān)測了降解菌在模擬含水層中遷移,實現了無擾動同時捕捉游離菌和附著菌的遷移動態(tài),首次直觀的揭示了生物強化的有效修復范圍;建立了一種新的運用皂素強化降解菌在含水層中遷移的技術方法,具有相對經濟、有效且環(huán)境友好的特點,并闡明了其強化機理;首次驗證了高效苯胺降解菌Pseudomonas migulae AN-1在模擬苯胺污染含水層中的存活、遷移和修復效能,系統且全面的研究了含水層中降解菌存活、降解菌遷移和生物強化修復效率三者之間的內在關系。綜上所述,本論文為實際生物強化原位修復苯胺污染地下水奠定了理論基礎,對實際工程應用具有重要的指導意義。
[Abstract]:With the rapid development of city economy and society, the serious pollution of groundwater due to the leakage of pollutants, especially widespread organic pollution, constitutes a serious threat to human safety of drinking water. Aniline is commonly used materials of modern agriculture, medicine and chemical products, a very wide range of applications, the pollution of groundwater due to cancer is relatively common. Aniline has on the human body, toxicity, mutagenicity and persistence in the environment, the prevention and control of groundwater pollution was affected by people's attention. In the remediation of groundwater contaminated by aniline method, physical repair technology of energy consumption and high cost of processing, chemical remediation technology is easy to cause two pollution on the environment, and in situ bioremediation due to its relative economic characteristics, effective and environmentally friendly and easy to repair and various means of combination, has obvious advantages. Among them, bioaugmentation through to the underground Exogenous degrading bacteria into the environment, to shorten the time to repair, improve the repair efficiency. However, the actual repair is often due to exogenous degrading activity in the added site and quantity is greatly reduced, lead to enhanced biological failure. Therefore, exogenous degradation bacteria in underground environment is vital to the survival and migration of bioaugmentation. Through the study on degrading bacteria in water containing survival, the relationship between migration and degradation bacteria bioaugmentation remediation efficiency of three, provide a theoretical basis for the actual biological remediation of groundwater pollution. Through the study of aniline ago showed that Pseudomonas migulae AN-1 is a cold, high efficient aniline degrading bacteria, in the low temperature the performance degradation is clear, the degradation conditions were also optimized, but the survival of AN-1 in the underground environment, and the migration of aniline contaminated aquifer on the repair efficiency is not yet clear. This paper studies the performance of AN-1 survival and migration in the aquifer; build a new green fluorescent protein (Green fluorescent protein, GFP) marker combination method system of optical projection technology, visual and real-time monitoring of the degrading bacteria in water in the simulation of migration, the first migration dynamic disturbance at the same time capture the free bacteria and attached bacteria, revealing the mechanism of migration in the aquifer degrading bacteria, has an important guiding significance to clear the scope and strengthen the regulation of repair of bioremediation; using saponin on degrading bacteria migration in the aquifer are strengthened by surface thermodynamic study of AN-1 liquid - solid medium three properties. The interface surface energy, Gibbs free energy and the DLVO interaction energy, and further clarified the mechanism for strengthening saponin migration, bioremediation and mitigation of Biological Clogging in theory and technology laid the foundation The basic investigation and verification of the AN-1; in the simulation of aniline polluted aquifer containing survival, migration and repair efficiency, establishes a relatively complete set of in situ bioremediation of aniline polluted groundwater system, has important reference value for the actual repair. Through the above research, this thesis mainly draws the following conclusions: the survival of AN-1 in aquifer in the migration and relevant characteristics of AN-1 can adapt to changes in the concentration of aniline, automatically adjust their cell membrane permeability, hydrophobicity and self aggregation of.AN-1 with the attached film forming ability of biofilm formation of AN-1, and also has good impact properties of aniline degradation and anti aniline. Groundwater in Ca2+ and SO42- (m M = 5) on AN-1 film role, the inhibitory effect of Fe2+. The migration mechanism of AN-1 in the aquifer by labeling with GFP optical transmission technology, without disturbance while capturing the simulated aquifer in the free and attached bacteria The dynamic migration of bacteria, intuitive and quantitative reveals the mechanism of AN-1 migration in the aquifer, the migration of degrading bacteria in the aquifer by its biological characteristics and groundwater convection, dispersion interaction, for the common effect of biological factors and hydrogeological factors. (1) degradation bacteria migration speed: AN-1 migration speed the ratio of groundwater flow fast and aquifer and the smaller the particle size of AN-1, promote the migration speed is bigger, faster and faster. The migration of AN-1 (2) degradation bacteria migration: the aquifer of larger particle size, groundwater flow is fast, the smaller the ionic strength in groundwater, dissolved organic matter more, the quality of AN-1 recovery in a saturated porous medium rate is greater, the coefficient of deposition rate is small, the more easy migration in the aquifer. The same ionic strength, the same anion, the two divalent cations than monovalent cations in inhibition of AN-1 migration; the same ionic strength, the same cation Two, anion than monovalent anions inhibit the migration of AN-1. (3) degradation bacteria dynamic migration: for the initial shape of the plume plume in bacteria, bacteria in the sand along the injection well to form a narrow band, in the sand to form a ellipsoid in underground injection part; for bacteria plume area. A linear relationship with time, and the injection amount in the same degrading bacteria, the same time, the same groundwater flow conditions in the sand in the area is larger than the range of bacteria for coarse sand; Yu, from the injection well to the degradation of feather fronts, which form a continuous microbial zone, including free plume region and the rear of the attachment of bacteria by region, has an important guiding significance to the clear repair scope and enhanced bioremediation. The regulation of AN-1 migration in the aquifer to strengthen saponin has no toxic effect on AN-1. When there are 0.3% or 0.1%, 0.5% saponin, AN-1 degradation rate of aniline is slightly higher than when no saponin, The biomass is slightly larger. The optimum concentration of 0.1% saponin washing solution, the concentration of AN-1 in liquid - solid medium three form interface surface energy of the system is minimum, Gibbs free energy, the minimum amount of bacteria retention method using 0.1% saponin flushing (without saponin pretreated for AN-1 direct injection containing water, then 0.1% saponin solution flushing), is to strengthen the AN-1 migration in the aquifer in the most economical, the most effective way. This method can make the AN-1 two effective migration in the aquifer, further expand the scope of strengthening the potential biological repair. Ion does not affect the function of promoting migration of saponin. When AN-1 saponin and ions, and ion alone compared to saponin significantly increased between AN-1 and medium particle energy barriers, the inhibition of AN-1 ion migration basically eliminated, promote AN-1 in saturated The migration in porous media. The AN-1 repair aniline contaminated aquifer in simulated aniline polluted aquifer, AN-1 can better survive, showed a good degradation performance, and can maintain the indigenous microbial community structure, make the population adapt to aniline impact. From injection well to degradation of plume fronts, can form a continuous microbial reaction with the effective range of the repair degrading bacteria free bacteria including the plume region and the rear of the attachment region. When injected in degrading bacteria in the aquifer polluted, degrading bacteria can adhesion growth and aggregation in the injection wells nearby, although the larger degradation rate of the area of aniline, the main degradation region, but may the formation of potential biological clogging. Degrading bacteria gathering area with water slowly moves downstream, and continue to expand, with peeling free cells, along with the water flow to the downstream migration of.AN-1 on aniline pollution water layer. Have good biological strengthening repair efficiency. The main innovation of this thesis lies in: to construct a new GFP marker combining method system of light projection technology, visual and real-time monitoring of the degrading bacteria in simulated migration in the aquifer, realizes dynamic migration without disturbance also capture free bacteria and bacterial attachment, the first intuitive to reveal the effective repair range bioaugmentation; establish a new use of saponin strengthen degrading bacteria migration in aquifer techniques, with relative economic, effective and environmentally friendly, and expounds its strengthening mechanism; the first to verify the efficient aniline degrading bacteria Pseudomonas migulae AN-1 in the simulation of aniline polluted with survival in the water, migration and repair efficiency, systematic and comprehensive research on water degradation bacteria survival layer, the intrinsic relationship between migration and degradation bacteria bioaugmentation remediation efficiency of three. To sum up This paper lays a theoretical foundation for the actual biological reinforcement of the remediation of groundwater contaminated by aniline in situ, and has important guiding significance for practical engineering applications.

【學位授予單位】:吉林大學
【學位級別】:博士
【學位授予年份】:2017
【分類號】:X172

【相似文獻】

相關期刊論文 前10條

1 楊震,唐學璽,宮相忠,方芳,呂文濤;褐藻酸降解菌引起海帶病爛的組織學研究[J];海洋科學;2000年12期

2 呂鳳霞,顧振新,方維明,汪志君;苦味苷降解菌的分離鑒定及其生長特性的研究[J];食品科學;2003年03期

3 劉新,尤民生,蔡志成,廖金英,魏英智;土壤中毒死蜱降解菌的誘發(fā)和持效期研究[J];生態(tài)學雜志;2004年01期

4 臧瑞玲;胡曉芳;印春生;蔡偉民;王艷;;農田土壤中辛基酚聚氧乙烯醚降解菌的分離[J];環(huán)境科學與技術;2006年04期

5 吳智誠;佘晨興;馬秀玲;陳盛;;機油降解菌的分離、篩選和鑒定[J];福建輕紡;2006年10期

6 秦華;林先貴;尹睿;陳瑞蕊;張華勇;王俊華;;接種降解菌對土壤中鄰苯二甲酸二異辛酯降解的影響[J];應用與環(huán)境生物學報;2006年06期

7 張祥勝;熊濤;;烴降解菌研究進展及低能離子束應用于誘變育種的設想[J];安徽農業(yè)科學;2007年32期

8 劉艷鋒;周作明;李小林;荊國華;方柏山;;芘降解菌的分離純化及其降解性能測定[J];華僑大學學報(自然科學版);2008年02期

9 王基成;張秀霞;房苗苗;吳偉林;趙朝成;魯軍;;兩株吡啶降解菌的分離與鑒定[J];生態(tài)環(huán)境;2008年01期

10 張秀霞;王基成;吳偉林;房苗苗;魯軍;;一株喹啉降解菌的分離與鑒定[J];農業(yè)環(huán)境科學學報;2008年03期

相關會議論文 前10條

1 臧瑞玲;魯春輝;胡曉芳;印春生;蔡偉民;王艷;;非離子表面活性劑辛基酚聚氧乙烯醚降解菌的分離[A];第二屆全國環(huán)境化學學術報告會論文集[C];2004年

2 D.J.Vaccal;W.F.Bleam;W.J.Hickey;霍煒潔;于江;;土壤中腐植酸吸附菲的降解菌的分離[A];第六屆全國綠色環(huán)保肥料新技術、新產品交流會論文集[C];2006年

3 王榮;張穎;任瑞霞;李慧;王新新;史榮久;徐慧;;利用載體吸附富集方法篩選土壤中芘降解菌的研究[A];第十次全國環(huán)境微生物學術研討會論文摘要集[C];2007年

4 趙平芝;李小會;張玲;朱曉飛;王睿勇;;溴甲烷降解菌的富集培養(yǎng)和分離篩選[A];2008年中國微生物學會學術年會論文摘要集[C];2008年

5 李體文;魏朝俊;賈臨芳;趙建莊;;丙環(huán)唑降解菌篩選的初步研究[A];農業(yè)環(huán)境與生態(tài)安全——第五屆全國農業(yè)環(huán)境科學學術研討會論文集[C];2013年

6 趙東岳;李勇;丁萬隆;劉敏;;人參自毒物質降解菌的篩選及其降解特性的初步研究[A];海峽兩岸暨CSNR全國第十屆中藥及天然藥物資源學術研討會論文集[C];2012年

7 趙野;鄧新平;胡國勝;;土壤中乙草胺降解菌的培養(yǎng)和篩選[A];慶祝重慶市植物保護學會成立10周年暨植?萍颊搲撐募痆C];2007年

8 王中華;梁靜兒;楊建強;周君;李成華;李太武;;原油微生物群落構成及降解菌降解特性的研究[A];2013中國環(huán)境科學學會學術年會論文集(第八卷)[C];2013年

9 李寶慶;鹿秀云;李社增;馬平;;甲醇降解菌的篩選、鑒定及其特性研究[A];第二屆全國農業(yè)環(huán)境科學學術研討會論文集[C];2007年

10 王新新;白鶴;李辰;趙麗彬;吳亮;韓增;安偉;陳宇;;耐鹽烴降解菌基因組學研究進展[A];2014中國環(huán)境科學學會學術年會(第十、十一章)[C];2014年

相關重要報紙文章 前1條

1 本報記者 王秋蓉;極地微生物研究六年終成正果[N];中國海洋報;2010年

相關博士學位論文 前10條

1 胡桂萍;氟氯氰菊酯降解菌FLQ-11-1分離鑒定、降解特性及降解機理[D];福建農林大學;2014年

2 劉芳明;3 株南極海洋石油烴低溫降解菌(Shewanella sp.NJ49、Pseudoalteromonas sp.NJ289和Planococus sp.NJ41)基因組學及比較研究[D];中國科學院研究生院(海洋研究所);2016年

3 靳競男;多環(huán)芳烴降解菌的篩選及基于靶標酶結構的降解機制研究[D];北京科技大學;2017年

4 曲丹;苯胺降解菌在含水層中的遷移機制及污染修復效能研究[D];吉林大學;2017年

5 袁軍;印度洋深海多環(huán)芳烴降解菌的多樣性分析及降解菌新種的分類鑒定與降解機理初步研究[D];廈門大學;2008年

6 許敬亮;多菌靈降解菌的分離、鑒定及其降解特性研究[D];南京農業(yè)大學;2006年

7 馬靜;多環(huán)芳烴降解菌的篩選、降解機理及降解性能研究[D];大連理工大學;2013年

8 侯穎;芳氧苯氧丙酸類和氯乙酰胺類除草劑降解菌的分離鑒定、降解基因克隆表達及其代謝途徑研究[D];南京農業(yè)大學;2011年

9 宋立超;鹽土多環(huán)芳烴降解菌篩選分離及其污染修復應用基礎研究[D];沈陽農業(yè)大學;2011年

10 駱苑蓉;多環(huán)芳烴降解菌的降解特性與降解途徑研究[D];廈門大學;2008年

相關碩士學位論文 前10條

1 趙永斌;3種四環(huán)素類抗生素降解菌的篩選及降解特性的研究[D];山西農業(yè)大學;2015年

2 呂勃熠;芳香烴降解菌的分離、鑒定及性質研究[D];天津理工大學;2015年

3 鄭瑞雨;渤海灣中柴油降解菌的降解性能及其固定化研究[D];燕山大學;2015年

4 張順;二氯喹啉酸降解菌篩選、鑒定和應用研究[D];中國農業(yè)科學院;2015年

5 黃現恩;幾株微囊藻毒素降解菌和溶藻菌的分離鑒定及作用效果[D];蘇州大學;2015年

6 賀艷艷;紅樹林沉積物中磺胺間甲氧嘧啶(SMMX)降解菌的篩選及其降解性能研究[D];廣東海洋大學;2015年

7 高悅;固定化原油降解菌的制備及其降解特性研究[D];吉林農業(yè)大學;2015年

8 孫國強;固定化降解菌Pseudomonas sp.DNB-S1對DBP污染土壤修復的研究[D];東北農業(yè)大學;2015年

9 段淑偉;鄰苯二甲酸二丁酯降解菌DNB-S1的篩選和其酶制劑的初步應用[D];東北農業(yè)大學;2015年

10 溫榮提;尼古丁降解菌Pusillimonas sp.T2的篩選、鑒定、降解特性及代謝途徑的初步研究[D];浙江工業(yè)大學;2015年

,

本文編號:1588102

資料下載
論文發(fā)表

本文鏈接:http://www.sikaile.net/shoufeilunwen/gckjbs/1588102.html


Copyright(c)文論論文網All Rights Reserved | 網站地圖 |

版權申明:資料由用戶416d6***提供,本站僅收錄摘要或目錄,作者需要刪除請E-mail郵箱bigeng88@qq.com