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研究生: Eka Viviantira
Eka - Viviantira
論文名稱: Denitrifying Sulfide Removal with Methanogenic Culture
Denitrifying Sulfide Removal with Methanogenic Culture
指導教授: 李篤中
Duu-Jong Lee
口試委員: 劉志成
none
黃志彬
none
張家修
none
朱曉萍
none
學位類別: 碩士
Master
系所名稱: 工程學院 - 化學工程系
Department of Chemical Engineering
論文出版年: 2011
畢業學年度: 99
語文別: 英文
論文頁數: 108
中文關鍵詞: 反硝化硝酸鹽甲烷基微生物多樣性硫化物
外文關鍵詞: denitrification, nitrate, methanogenic, microbial diversity, sulfide
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使用加入了硝酸鹽或/及硫化物的甲烷基批式培養槽,可同時去除硫化物、硝酸鹽、碳。加了硫化物的培養槽,濃度範圍50—500mg N/L的硝酸鹽可有效地做反硝化形成氮氣。從這反應機制可提出反硝化作用發生,自營為第一途徑,異營為第二途徑。經探討微生物群得知自營反硝化途徑經由epsilon proteobacterium (例如 Thiomicrospira denitrificans)進行。 在有加硫化物和沒加硫化物的培養槽中,異營反硝化途徑皆藉由Thauera sp.發生。
在沒有硫化物且硝酸鹽初始濃度在250 mg N/L 的培養槽中, 硝酸鹽還原途徑會稍微轉移到DNRA上。若長時間移除硫化物,且留下硝酸鹽類,在開始實驗後32小時硫化物會還原成元素硫。經由活性硫酸鹽還原菌的異營養化途徑,之後可近乎恢復成初始濃度。為了能達到完全去除硫化物,在硫酸鹽還原菌活性提高之前,元素硫產生需要先被移除。在培養槽添加硝酸鹽初始濃度750和1000 mg N/L 的情況下, 由氮氧化物中間體可觀察到這種菌株活動的抑制。這種抑制則不會讓硫化物恢復。
在產生甲烷時,單加入硝酸鹽濃度50—500mg N/L 導致延遲甲 烷基機制。於硝酸鹽濃度750—1000 mg N/L下,則會完全發生抑制。 此外,於濃度100mg S/L硫化物下加入硝酸鹽類會減少甲烷產生, 而在濃度200mg S/L硫化物會發生嚴重抑制甲烷生成。 然而, 當只有硫化物單獨加入時,抑制沒有添加硝酸鹽類那麼嚴重。在所有培養槽中,由於反硝化反應是抑制中間體,主要是亞酸鹽和氮氧化物累積。由此可說明,第一次發生反硝化作用亦可同時抑制甲烷基。


Simultaneous sulfide, nitrate and carbon removal in the effect of nitrate and/or sulfide addition using methanogenic cultures was investigated using batch cultures. In cultures supplemented with sulfide, 50--500 mg N/L nitrate efficiently denitrified to nitrogen gas. The mechanism proposed was denitrification occurred via autotrophic pathway first, followed by heterotrophic pathway. Microbial community probing suggests that autotrophic denitrification were carried out by epsilon proteobacterium (for example Thiomicrospira denitrificans). The heterotrophic pathway was carried out by Thauera sp. in both cultures with and without the addition of sulfide.
Nitrate reduction pathway slightly shifted to DNRA in cultures with no addition of sulfide, starting at intial nitrate concentration 250 mg N/L. In term of sulfide removal, with the presence of nitrate, sulfide was reduced to elemental sulfur in 32 hours after the assay began. Due to the activity of sulfate reducing strains, it was later recovered back to nearly initial concentration via heterotrophic oxidation pathway. To achieve complete sulfide removal, elemental sulfur yielded need to be removed before sulfate reducing strains become active. Suppression to this strain activity due to N-oxides intermediates was observed on cultures supplemented with nitrate at initial concentration of 750 and 1000 mgN/L. This suppression then leads to no sulfide recovery.
On methane production, sole addition of nitrate at concentration 50--500 mg N/L resulted in delay of methanogenesis. At concentration 750--1000 mg N/L, a complete suppression occurred. Addition of nitrate along with sulfide at concentration 100 mg S/L decrease methane production, while at concentration 200 mg S/L, severe inhibition occurred. However, when sulfide was dose alone, the inhibition was not as severe as when it was added with nitrate. In all cultures, inhibition was due to denitrification intermediates, mainly by accumulation of nitrite and nitrous oxide. This strongly suggests that denitrification occurred first while at the same time inhibit methanogenesis.

ABSTRACT i ABSTRACT IN CHINESE iii ACKNOWLEDGEMENTS v TABLE OF CONTENTS vii LIST OF FIGURES ix LIST OF TABLES xi CHAPTER 1 INTRODUCTION 12 CHAPTER 2 LITERATURE REVIEW 16 2.1 Nitrogenous contaminants 16 2.2 Sulfuric compounds 18 2.3 Removal of nitrogenous and sulfuric compounds from wastewater 19 2.4 Microbial community probing 25 CHAPTER 3 MATERIALS AND METHODS 27 3.1. Methanogenic culture 27 3.2. Batch Assays 28 3.3. Analyses 30 3.3.1 Gas Analyses 30 3.3.2 Liquid Analyses 31 3.4. DNA extraction, PCR, DGGE and sequence analysis 33 3.4.1. DNA extraction and PCR 33 3.4.2. DGGE 35 3.4.3. Cloning and sequence analysis 36 CHAPTER 4 RESULTS AND DISCUSSION 37 4.1 Sulfide free culture 37 4.2 Sulfide added culture 44 4.3 Microbial Community 61 4.3.1 PCR-DGGE bands 61 4.3.2 Microbial Community Identification 68 4.3.2.1 Bacteria domain 69 4.3.2.2 Archaea Domain 86 CHAPTER 5 CONCLUSIONS 90 REFERENCES 91

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