TW438621B - Purification method for contaminants caused by halogenated organic compounds - Google Patents

Purification method for contaminants caused by halogenated organic compounds Download PDF

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Publication number
TW438621B
TW438621B TW87101140A TW87101140A TW438621B TW 438621 B TW438621 B TW 438621B TW 87101140 A TW87101140 A TW 87101140A TW 87101140 A TW87101140 A TW 87101140A TW 438621 B TW438621 B TW 438621B
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Taiwan
Prior art keywords
alloy
aforementioned
soil
original
agent
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TW87101140A
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Chinese (zh)
Inventor
Naoaki Kataoka
Tatsuo Shimomura
Nobumitsu Kitajima
Naoki Seki
Hiroshi Shinmura
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Ebara Corp
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Priority claimed from JP02536797A external-priority patent/JP4021511B2/en
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Publication of TW438621B publication Critical patent/TW438621B/en

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Abstract

A method for purifying matter contaminated with a halogenated organic compound is disclosed. The method includes the step of adding a reducing agent and a nutritional source for a heterotrophic anaerobic microorganism to the contaminated matter. The reducing agent is reduced iron, cast iron, iron-silicon alloy and so on, or a water soluble compound. A combination of chemical reactions with microorganisms allows to decompose the halogenated organic compound. The nutritional source including an organic carbon and 20 to 50 percent by weight of an oxidized form of nitrogen is added, thereby preventing by products of the decomposition such as generation of noxious gases and decoloration of soil. A method includes the steps of mixing a reducing agent and a nutritional liquid with the contaminated matter, wherein the mixing step including a step of adjusting the contaminated matter at pH ranging from 4.5 to 9.0; and keeping the mixture in a condition that air hardly penetrates through a matrix, thereby allowing to uniformly mix a large amount of the contaminated matter.

Description

經"·部中决#準局員^消费合作牡印" 4 3 8 6 2 1 A7 B7 五、發明説明(1 ) 發明夕抟術領城 本發明為闞於一種淨化因鹵化有櫬物,尤其是含氛有 機物污染之污染物,例如土壤、沈積泥、污泥、水之方法 ,此淨化法為闞於一種由化學反麽结合生物性反應之特別 的運原性脫鹵化反應f以分解因鹵化有機物污染之污染物 Ο 已件枝衡 近年來相繼有報告Μ於因廣泛使用在電子櫬械金雇零 件之脫脂、清潔劑及乾洗淸潔劑中之四氯乙烯、三氛乙烯 、1,1,1-三氣乙烷、二氣乙烯等含鹵素有櫬化合物而污染 土壤、地下水道。此等含鹵素有櫬物因在自然界中不易分 解、且難溶於水,而易於積存於污染區域之土壤中或滲透 入地下水中。又,含鹵素有機物可引起肝臟損害,且有致 癌性。因此之故,一般人期望可Μ將土壤中所含之含氛有 櫬物等鹵化有機物分解。 最近,此微生物處理法(生物化育)淨化因鹵化有櫬物 污染之土壤、地下水道等的污染物淨化法受到矚目。雖然 激生物處理法亦有相對於效果、安全性之費用高。但是微 生物處理法亦有如下述之處理期間長、可分解物質之種類 及濃度之限制,因此未必可以令人完全滿意。 該微生物處理法之一例為在多數報告中關於甲烷利用 性菌及甲苯、酚分解菌、氨氧化细菌、烯類利用性菌以好 氣性分解三氯乙烯之方法。然而其缺點為:1)分解反應不 安定、2)分解對象物質之範園搔小、3)對四氛乙烯或四氢 本紙張尺度適用不國國家標準(CNS ) Α4規格(210Χ297公釐) " (請先閱讀背面之注意事項再填寫本頁} ’1Τ A7 438621 B7 五、發明説明(2 ) 化碳之高氯化物質無分解作用。 另一方面,有多棰厭氣性微生物對四氯乙烯、三氛乙 烯、四氛化碳等高含氛有機物有廣泛之分解作用。但仍有 :1)微生物之繁殖非常媛慢、2)厥氣性分解過程中會產生 、積存高毒性中藺代謝產物等缺點(内山裕夫、矢木修身 、生物.科學與產業(Biosciance and Induotriy)、 1994年 、第52卷,第11號,第8 7 9〜88 4頁)。 另一方面,闥於利用化學反應分解含鹵素有機化合物 之技術,有報導係以金鼷鐵通原處理含氯有機物(先崎哲 夫、有機氛化物污染地下水之處理一 Μ含金屬鐵活性碳在 低溫處理之技術、「PPM」、1995年、第26卷,第5號, 第64〜70頁)。因此,本發明之發明人試驗微生物在無碳 源狀態下於土壤中添加金_級進行脫氯試驗。然而,微生 物在非培着條件下,特別是不維持在堪原環境及中性條件 之埸合中,並未發現有脫氛反應。又即使添FeCU、FeCl3 、FeS〇4之鐵塩取代金屬塩的場合,亦未發現有脫氯反應 Ο 再者,亦有報導將金觸鐵與高颳空氣灌人受污染的土 壤中使含鹵素有機化合物與截粉反應,將其礦化之無害化 處理方法(日本恃開平8-257570號)。但在該方法中仍有將 空氣灌入之設備問題及含鹵素有櫬化合物飛散的顧盧等問 題。甚且,因使用髙壓空氣,而有成本上之問題產生,並 不實用。 此外,亦有報告结合具脫鹵催化作用之天然物質與微 (請先閲讀背而之注意事項再填寫本頁) '11 經Μ部中次標準局员Η消費合作社印來 本紙張尺度適用中國國家標準(CNS ) Α4規格(210X 297公漦) 2 39498 438621 A7 經Μ部中"標準局負工消费合作社印製 B7五、發明説明(3 ) 生物處理,Μ去除受污染土壤及地下水之有慊含氣化合物 的方法(「日經生物技術」(日經ΒΡ公司發行>1996年10月? 日發行、第361號第14〜15頁)。然而其中對所有的天然物 質及微生物均無具體之記載。 在美画專利第5,411,644號中則記載著將纖維性有機 物及鐵等多價金靥粒子添加在污染物中,Κ分解其中含鹵 素有機化合物之方法。但在該美國專利中並未記載堪原截 。生嫌、合金、水溶性堪原劑等還原劑。而且亦無記載醆 於在添加遢原劑後,如何保持污染物在遢原環境及特定的 ρ Η 〇 再者,添加之營養涯的成份.可能在土壤中發生硫酸 埵原、甲烷醱酵等生物性进原反應,而產生硫化氫、碇醇 等硫磺系惡臭氣體或甲烷等可燃性氣體。又,土壤亦可能 因伴隨產生硫化嫌而變色為黑色。甚至亦可能因金屬粉末 與水反應而產生可燃性之氫氣。 再者又以,在實驗室內可容易地將遢原劑、營養源及 污染物均勻混合。相對地,實際上為淨化土壤等之污染物 ,必須有將大量的還原劑與曾養源琨合之土木工程。又欲 予均勻地混合並非容易。再者,可Μ預想混合時的條件必 影響含鹵素有機化合物之分解率。尤其欲淨化la3M上體 横,或甚至10m3M上體積之污染物時,即必須考《混合方 法。 發明之K咯 /本發明之目的,在於提.供一棰结合化學反應及生物性 本紙張尺度適用中國國家標準(CNS ) A4規格(210X297公釐) 3 39498 (讀先閲讀背面之注意事ο再填寫本頁)经 "· 部 中 定 # 准 局 员 ^ Consumer Cooperation Mu Yin" 4 3 8 6 2 1 A7 B7 V. Description of the Invention (1) Invention of this invention , Especially pollutants containing contaminated organic matter, such as soil, sediment, sludge, and water. This purification method is based on a special transportable dehalogenation reaction combining chemical reactions with biological reactions. Decomposes pollutants contaminated by halogenated organics. There have been reports in recent years. In the degreasing, cleaning agents, and dry cleaning detergents widely used in electronic machinery parts, tetrachloroethylene, three atmosphere ethylene, 1,1,1-three gas ethane, two gas ethylene and other halogen-containing rhenium compounds pollute the soil and groundwater channels. These halogen-containing compounds are difficult to decompose in nature and are hardly soluble in water, so they tend to accumulate in the soil of contaminated areas or penetrate into groundwater. In addition, halogen-containing organic substances can cause liver damage and are carcinogenic. For this reason, it is expected that halogenated organic compounds such as tritium compounds contained in soil can be decomposed. Recently, the microbial treatment method (biochemical breeding) has attracted attention as a method for purifying pollutants such as soils and groundwater channels contaminated by halogenated tritium. Although the stimulant treatment method also has a high cost relative to the effect and safety. However, the microbiological treatment method also has the limitation of a long treatment period and the types and concentrations of degradable substances as described below, so it may not be completely satisfactory. An example of this microbial treatment method is a method in which methane-utilizing bacteria and toluene, phenol-decomposing bacteria, ammonia-oxidizing bacteria, and ene-utilizing bacteria decompose trichloroethylene aerobically in most reports. However, its shortcomings are: 1) unstable decomposition reaction, 2) Fan Yuanzhang, which is the target substance of decomposition, 3) the national standard (CNS) Α4 specification (210 × 297 mm) is applicable to the paper standard of tetra atmosphere ethylene or tetrahydro. " (Please read the notes on the back before filling in this page} '1Τ A7 438621 B7 V. Description of the invention (2) Highly chlorinated substances of carbonized carbon do not decompose. On the other hand, there are many anaerobic microorganisms which High-atom organic materials such as tetrachloroethylene, tri-atom ethylene, and tetra-atomized carbon have a wide range of decomposition. However, there are still: 1) very slow reproduction of microorganisms, 2) high toxicity produced during the decomposition process Disadvantages of Nakayama metabolites (Uchiyama Yufu, Yagi Slim, Biosciance and Induotriy, 1994, Vol. 52, No. 11, No. 8 7 9 ~ 88 4). On the other hand, the technology of decomposing halogen-containing organic compounds using chemical reactions has been reported to treat chlorine-containing organic compounds with Takihara Tsubakihara (Tsaki Saki, organic atmosphere contaminated groundwater, 1M metal-containing activated carbon at low temperature Technology, "PPM", 1995, Vol. 26, No. 5, pp. 64-70). Therefore, the inventors of the present invention tested the microorganisms by adding gold to the soil in a carbon-free state to perform a dechlorination test. However, under non-cultivated conditions, especially in the combination of the original environment and neutral conditions, no deaeration reaction was found. Even when Fe 即使, FeCl3, and FeS〇4 were added instead of metal 塩, no dechlorination reaction was found. Furthermore, there have been reports that gold-touched iron and high scraping air were irrigated into the contaminated soil. Harmless treatment method for halogenated organic compounds to react with powder cuts to mineralize them (Japanese Kaikai Hei 8-257570). However, in this method, there are still problems with equipment for injecting air and Gu Lu with the scattering of halogen-containing europium compounds. Furthermore, the use of pressurized air causes cost problems and is not practical. In addition, there are also reports combining natural substances with micro-dehalogenation and micro-organisms (please read the precautions on the back and then fill out this page) '11 Printed by the member of the Ministry of Intermediate Standards Bureau, Consumer Cooperatives, this paper applies to China National Standard (CNS) A4 Specification (210X 297 Gong) 2 39498 438621 A7 Printed by B in the Ministry of Standards " Standards Bureau Consumers Cooperatives Co. B7 V. Invention Description (3) Biological treatment, M removes contaminated soil and groundwater There is a method for gas-containing compounds ("Nikkei Biotechnology" (issued by Nikkei BP & Co., Ltd. > October 1996? Issued, No. 361, pp. 14-15). However, all natural substances and microorganisms are There is no specific record. US Patent No. 5,411,644 describes a method of adding fibrous organic matter and iron and other multivalent gold tincture particles to pollutants to decompose halogen-containing organic compounds. However, in this US patent There is no record of Kanbara. Reducing agents such as biogenics, alloys, and water-soluble Kangen agents. There is also no record of how to keep the pollutants in the Harahara environment and a specific ρ Η after adding the rhenium agent. In addition, the added nutritional ingredients may occur in the soil, such as sulfonium sulfate, methane fermentation, and other biological advancement reactions, and produce sulfur odor gases such as hydrogen sulfide, methanol, or combustible gases such as methane. Also, soil It may also become black due to the accompanying sulfidation. It may even generate flammable hydrogen due to the reaction of metal powder with water. Furthermore, in the laboratory, it is easy to combine primogens, nutrients and pollutants in the laboratory. Uniform mixing. In contrast, in order to purify pollutants such as soil, there must be a civil engineering that combines a large amount of reducing agent with the former source. It is not easy to mix uniformly. Furthermore, when mixing is expected The conditions will affect the decomposition rate of halogen-containing organic compounds. Especially if you want to purify the la3M upper body horizontal, or even the volume of pollutants on the 10m3M volume, you must consider the "mixing method. The invention of K slightly / the purpose of the present invention is to improve. For the purpose of combining chemical reactions and biological properties. The paper size applies the Chinese National Standard (CNS) A4 specification (210X297 mm) 3 39498 (Read the precautions on the back first before filling in this )

,1T ί 43 86 2 1 Α7 明説 明發 、五 物 合 化 機 有 化 鹵 因 化 淨 物 合 化 櫬 有 素 鹵 含 解 分 Μ 應 反 法 方 之 物 染 污 的 起 引 染 污 應 反 化 鹵 脫 性 原 堪 由 為 的 巨 其 搛 態 1 第 之 明 發 本 物 合 化 櫬 有 素 鹵 含 解 分 應 反 化 鹵 脫 性 學 化 由 為 的 其 樣 態 2 第 之 明 發 本 物 化 機 有 素 鹵 含 解 分 應等 反壤 化土 鹵及 脫以 性 , 原體 通氣 止性 防燃 為可 的成 目 生 其或 , 體 樣氣 態臭 3 惡 第系 之磺 明硫 發的 本生 畐 中 等 色 變 度 通 之 物 染 污 合 埸 之 物 染 樓 。 « 合 大 混 在物 為染 的污 目與 其劑 , 原 樣缠 態及 4 源 第着 之營 明將 發地 本效 有 由0 原 埋 的 定 特 加 添 於 在 激 特 其 樣 態 第 明 發 本 應 反 化 鹵 脫 性 原0 進 促 Τ"Τ\ 以 爾 原 遢 的 定 特 加 添 於 在 擻 特 其 樣 態 2 第 明 發 本 必 化 不由 , 僅 同 , 不劑 樣原 態還 1 的 第定 明特 發用 本使 與 〇 但可 〇 亦 應關 反相 化應 鹵 反 脫性 性物 學生 化與 進定 促 1 物 化 機 有 素 鹵 含 解 分 可 即 應 反 學 (#先閲讀背.7"注意事項再填寫本頁), 1T ί 43 86 2 1 Α7 It is clearly stated that there is a halogen in the hair and five-in-one combination machine, a net product is combined with a chemical compound, a halogen-containing compound is decomposed, and the halogenated material should be decontaminated. Proteomics can be considered as a state of greatness 1 The first manifestation of the present invention should be combined with a halogen-containing solution. The halogenated solution should be reversed. The second aspect of the present invention is well-organized. The halogen-containing solution should be equal to the anti-loaming soil, the halogen, and the dehydration, the original body ventilation and flame retardation may be possible, or the body-like gaseous odor. The things with the same degree of color change stain the buildings with the combined things. «Heda Mixture is stained with stains and its agents, as it is, and the original source of the 4th source of the book Mingying will be added to the original effect of 0 from Dingte buried in the original state of the book Halogen degeneration should be reversed to promote the quotation of T " T. The original characteristics of the original are added to the special state of the 2nd, the first manifestation of the inevitable, but the same, not the same as the original state of 1 Determining the special issue of the book with 〇 but can 〇 should also be related to the inversion of the halogen should be reversed, and the student should be promoted. 1 The physical and chemical machine has a good halogen, and it can be reversed (# 先 读(Back.7 " Notes before filling out this page)

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或 者 » 最 好 在 第 1 階 段 步 驟 中 在 前 述 污 染 物 內 添 加 1 ! | 混 合 刖 述 污 染 物 量 之 1〜5 體横%的前述營養液, 其次第 讀 1 1 I 2 階 段 之 步 嫌 則 在 i * 刖 述 污 染 物 中 添 加 1 混 合 與 第 1 階 段 合 先 閱 讀 1 1 1 計 為 1 J. 刖 述 污 染 物 量 之 5〜10體積%的前述曾養液, 再者在 背 -之 J W·· 月U 述 污 染 物 中 添 加 混 較 第 1 階 段 或 第 2 階 段 更 多 量 的 注 意 事 1 * 1, 前 述 曾 着 液 〇 項 再 填 1 1 此 外 t 刖 述 通 原 劑 Μ 水 溶 性 化 合 物 1 或 前 述 m 原 劑 以 寫 本 頁 1 溶 解 於 前 述 營 養 液 中 者 為 佳 〇 另 外 1 Λ.*· 刖 述 靜 置 步 驟 中 t Λ, «· 刖 、^ 1 I 述 污 染 物 在 至 少 開 始 之 3 曰 内 Μ 保 持 於 17 Q0V 為 佳 0 1 1 I 本 發 明 之 第 4 態 樣 中 r u- 刖 述 汚 染 中 添 加 之 前 述 曾 養 液 1 1 訂 1 >λ 最 终 為 前 述 污 染 物 量 之 15 25體積% 為 佳 〇 又 ·> 月U 述 靜 置 步 驟 中 » 在 至 少 最 初 之 5 曰 內 保 持 前 述 1 1 污 染 物 在 17 60 Ό 為 佳 0 此 外 * 在 前 述 靜 置 步 驟 中 1 Μ 至 1 | 少 在 最 初 之 3 曰 内 t 或 最 好 在 5 曰 內 t 保 持 前 述 污 染 物 在 岫、 20 4〇 υ 為 佳 0 | 前 述 靜 置 步 驟 >λ 與 周 圍 為 隔 雛 狀 態 進 行 為 佳 0 為 維 持 1 1 低 通 氣 條 件 9 月IJ 述 污 染 物 外 最 好 包 覆 不 通 氣 材 料 0 將 刖 述 1 1 污 染 物 浸 於 水 性 液 Η 内 維 持 低 通 氣 條 件 亦 佳 〇 刖 述 污 染 物 1 1 以 在 容 器 中 與 A * 月IJ 述 營 養 液 > >-刖 述 還 原 劑 混 合 為 佳 0 1 1 η 式 簡 單 說 明 1 第 1 画 所 示 之 圖 為 依 照 本 發 明 9 將 四 氣 乙 烯 污 染 土 壤 1 I Μ 甲 烧 生 成 用 培 養 基 在 厭 氣 條 件 下 試 驗 适 原 性 脫 齒 化 反 應 1 1 I 之 結 果 σ 1 1 本紙張尺度適用中國國家標準((.:NS ) Λ4規格(2丨0><297公漦) 9 3 9 498 4386 2 1 A7 B7 經消部中决標準局負T,消贽合作牡印製 五、發明説明(10 ) I 第 2 圖 所 示 之 圔 為 依 照 本 發 明 9 將 四 氛 乙 烯 汚 染 土 壤 1 1 以 硫 酸 遒 原 培 養 基 在 厭 氣 條 件 下 試 驗 脫 鹵 化 反 應 之 試 驗 结 1 I | 果 〇 讀 先 閡 1 i I a. 明 害 m 形 想 1 | 讀 1 \ 本 發 明 之 第 1 m 樣 第 2 態 漾 > 及 第 3 態 揉 為 因 鹵 化 背 1 有 襪 化 合 物 污 染 物 之 淨 化 〇 本 說 明 書 中 之 鹵 素 指 氣 、 氛 V 注 意 事 1 *丨_ 溴 N 磺 〇 本 發 明 可 以 淨 化 含 鹵 素 原 子 有 m 化 合 物 之 染 物 項 再 1 * 特 別 可 Μ 淨 化 含 氯 原 子 及 溴 原 子 有 機 化 合 物 之 污 染 物 i 本 頁 V 更 特 別 可 >λ 淨 化 含 氣 原 子 有 懺 化 物 之 污 染 物 〇 該 氣 化 有 、- 1 I 機 化 合 物 不 限 於 例 如 - 四 氛 乙 烯 三 氣 乙 烯 1 , 1 , 卜 二 氛 1 1 J 乙 烷 二 氯 乙 烯 等 脂 肪 族 化 合 物 f 五 氯 酚 等 芳 香 族 化 合 物 1 1 亦 可 以 分 解 〇 訂 1 本 發 明 第 1 態 樣 第 2 態 樣 \ 第 3 態 樣 及 第 4 態 樣 可 I 1 以 處 理 的 污 染 物 有 : 土 壞 底 泥 \ 污 泥 等 〇 此 外 t 堆 肥 1 | 堆 m 化 有 櫬 物 m 棄 物 等 亦 可 以 處 理 〇 另 外 » 本 發 明 第 1 態 樣 Ί 第 2 態 樣 及 第 3 態 樣 亦 可 以 處 理 地 下 水 、 m 水 等 水 ,Ί 1 性 液 艟 〇 本 說 明 軎 中 之 水 性 液 ϋ 則 包 括 • 水 溶 液 \ 懸 浮 液 1 i 1 % 乳 化 液 及 其 混 合 物 〇 1 1 污 染 物 為 土 壤 、 底 泥 、 污 泥 等 之 場 合 1 含 水 率 Μ 至 少 1 1 在 25重 量 % 以 上 為 佳 , 40 60% 重 噩 % 更 佳 0 為 繁 殖 厭 氣 1 1 性 微 生 物 ψ 土 壤 污 泥 等 之 中 以 空 氣 不 易 進 入 的 狀 態 為 佳 1 I 〇 其 中 之 含 水 率 (% )如 下 定 義 〇 1 I 含 水 率 = (水份重量/含水份污染物重量)Χ 100 1 1 1 W· 刖 述 污 染 物 為 地 下 水 Λ m 水 等 之 場 合 , 含 水 率 必 定 在 1 ! 本紙張尺度適用中國國家標準((.’NS ) Α4規格(2f〇X297公釐) 10 3 9 498 烀漓部屮"標卑局員工消费合作社印^ 4 3 8 6 2 1 a? B7五、發明説明(11 ) 25重量% Μ上。 本發明第1態樣中,前述污染物中添加在25Τ下其對 標準氫電極之標準電極電位為130bV--2400η\ί之遨原劑、 及從羼營養型厭氣性微生物的營養源,Μ促進化學反應及 生物性反應甬者,分解鹵化有櫬化合物。 物質之機準電極電位在較130bV高的場合,則無法得 到充份的還原力。另一方面,物質之標準電極電位較 -2400iV低,例如:金鼷納、金靥鉀等鹹金鵰類,則由於 遢原力太強,遇水易發生燔發性反應而產生氫氣,極為危 險,因此不宜。25它下對標準氫電極之檷準電槿電位(Ε°) 如下表所示。 (請先閱讀背面,之注意事項再填寫本頁) 本紙張尺度適用中國國家標準(CNS ) Α4規格(210X297公釐) 39 498 438621 A7 B7五、發明説明(12 ) 25C下標準氫電極之檷準霣極電位(ε°) 經碘部中决標準局貞工消費合作拉印"' 霣槿反應 E° UV) Ca2 + + 2&~<r Ca -286 5 Na+ + e- <- -> Na -2714 Hg2+ + 2e_ — 4 Mg - 23 63 Al3 +3e~<-->Al -1662 Z n 2 + 2e-^ Zn -763 Fe^+ + 2e-^- Fe -440 Cd2 + + 2e-<- -> Cd -403 N i 2 + 2 e - f N i -250 Sn2+ + 2e~ <r Sn -136 Fe3 + + 3e-<- — Fe -36 2H + + 2e'^ -> H2 0 抗壊血酸(pH7 . 0) 58 (請先閲讀背面之注意事項再填寫本頁) '11 所謅摞準電極電位,亦即在Μ於電池反應中,與電池反應 相鼷之各化學種在檷準狀態(純固相、檷準濃度、標準壓 力等)之下,Κ氬電極為比較電極測定之場合所测定的電 位做為檷準電位Ε。。此值可ΜΜ下式表示之。 Ε° ~ - Δ G° / nF 其中,AG。為電池反應之檷準Gibb’s自由能變化, 12 本紙張尺度通用中國國家標準(CNS ) A4規格(210X297公釐) 3 9 498 438621 A7 ____ B7 五、發明説明(丨3 ) η為反應相闞之電子數,F為法拉第常數。必須要注意的 是,通常,氧化逐原電位以飽和氮化銀電極為比較電極測 定之電位表示的場合為多,此場合時測定的數值較以氫播 準電極為比較電極測定所示之檷準電位約低2〇〇niV程度。 本發明中前述《原劑為通原嫌、生戡、嫌一矽合金、 钛合金、鋅合金、錳合金、鋁合金、鎂合金、鋁合金及水 溶性化合物之群體中選擇的至少1種。 前述堪原劑,Μ在251下對標準氫電極之禰《電極電 位為_400nV〜~2400biV之金麵物質為佳。 本發明實腌樣態之一,使用适原_為遢原劑、截粉通 常因表面氧化而形成氧化皮瞑。相對地,運原鏹之氧化皮 (諳先閱讀背面之注意事項再填寫本頁) 種化 * 量購 佳»用 去 堅 一 , 以含司 為 ,利 除 的? Ϊ 可之公 劑外再 質 成 _ 為亦嫌限 原此M雜 形 ®)o嫌中有 堪。可 中 而大司 化其份 之率屑 其 原 β 公氧 ,股 截化戡 將 限之锇業 生淨此 再 之化 有原原 Η 用高。 , 物氧份還堪蕖 使成佳 锇 化易股 受的純Μ達更 銑 氧極販。謂光 -可則 之 由而出質所和 中時屑 成 。 指狀立物。自 態同嫌 造 高 ,末共之搛可 樣 ,生 製 性孅粉 ,原化: 施理即 原 想原之會适氧如 實處亦 遢 反還 细員氣於例 他於- 石 ,的微委氫限其 其易Μ確 化譖極輯受不。 之且削 嫌 氧所為鑷可並上 明全切 將 易此、典下物 Κ 發安之 般 、 在嫌辭溫化 % 。本嫌品 一 少 屬大高氧90者 生物 膜 金學的但在得 。造。 本紙張尺度適用中國國家標準(CNS ) Α4規格(2】0XW7公釐) 13 3 9498 438621 A7 B7 經漭部中决標率局負T.消費合作私印挈 五、發明説明(14 ) 1 1 即 成 為 產 業 利 用 性 之 鐵 » 碳 m 度 在 約2% (重 董 )Μ下者為 1 1 | m 、 含 碳 在 此 Μ 上 者 謂 之 生 m ( 「理化學辭典」 第4 版, I I | 1 9 87 年 9 第411頁)。 鋼 之 檄 械 性 質 較 佳 > 可 加 工 利 用 為 多 請 1 1 1 數 之 工 業 製 品 0 在 探 討 利 用 切 削 之 m 屑 於 淨 化 因 鹵 化 有 機 先 閱 讀 I 1 1 化 合 物 引 起 的 污 染 物 霣 之 方 法 中 % 卻 因 切 削 加 工 中 使 用 油 背 之 9 故 鋼 製 品 之 切 削 屑 中 有 油 〇 因 肚 使 用 在 本 發 明 因 有 機 氛 注 意 事 1 ^ |. 化 合 物 引 起 的 污 染 物 之 淨 化 方 法 時 可 能 因 油 而 引 起 2 次 項 再 ύ 1 [ 污 染 Ο 相 對 地 9 鐳 造 使 用 之 生 嫌 1 因 為 不 使 用 切 削 加 工 時 寫 本 頁 I 的 油 » 不 虞 生 嫌 m 品 之 切 削 屑 (生嫌屑) 引 起 的 如 前 述 m m 1 1 I 品 切 削 屑 之 2 次 污 染 0 1 1 本 發 明 之 其 他 實 施 樣 態 可 使 用 合 金 為 m 原 m 0 亦 即 可 1 1 以 使 用 嫌 一 矽 合 金 、 钛 合 金 鋅 合 金 S 錳 合 金 \ 鋁 合 金 訂 1 鎂 合 金 及 鈣 合 金 0 鈦 合 金 例 如 紋 矽 合 金 > 钛 — 鋁 1 ! 合 金 〇 鋅 合 金 t 例 如 鋅 一 鋁 合 金 〇 錳 合 金 • 例 如 : 錳 — t | 鎂 合 金 0 鋁 合 金 * 例 如 铝 — 鋅 — 鈣 合 金 鋁 — 錫 合 金 > 鋁 一 矽 合 金 等 0 鎂 合 金 ♦ 例 如 : 鎂 — 錳 合 金 ΰ 鈣 合 金 1 例 \ } -1 I 如 鈣 — 矽 合 金 〇 1 1 堪 原 劑 之 作 用 可 Μ 逐 原 锇 之 場 合 為 例 說 明 〇 金 屬 嫌 之 1 J m 氣 脫 鹵 化 反 應 之 反 應 機 制 中 * 遢 原 截 之 反 應 依 據 先 崦 之 1 1 報 告 ( 「有機氯化合物污染地下水之處理- ~ Μ金靨搛附著 1 I 活 性 碳 在 低 溫 下 之 處 理 技 術 J PPH, 1 9 95 年, 第26卷, 1 I 第 5 虢 1 第 64 70頁 ), 缠原娥之表面會發生鹵化有櫬化 1 I 合 物 之 吸 附 » 同 時 由 於 m 原 嫌 表 面 金 藤 方 面 與 環 境 方 面 之 1 1 I 條 件 差 異 會 發 生 陽 極 與 陰 極 之 分 極 > 因 此 會 有 電 流 潦 動 〇 I 1 14 本紙張尺度適用中國國家標準(CNS ) Λ4規格(2】0Χ 297公釐) 3 9 498 4 3 8 6 2 1 a7 B7 經,%·部中"桴津局貞-τ·消费合作社印來 五、發明説明(I5 ) 1 I 同 時 陽 極 上 m 形 成 1 離 子 溶 解 f 陰 m 上 則 潦 入 電 子 9 因 1 I tt 發 生 脫 鹵 化 反 應 等 1 通 原 反 應 0 1 1 I 陽植: F e F e2 + + 2 e _ 諳 I 1 | 生 m 如 前 述 指 含 碳 濃 度 在 2%以上者, -般為重量之 先 閲 ik 1 t [ 3 Λ -3 .596 » 容 量 則 為 石 墨 , 包 含 13 -W 14% 之 大 量 碳 0 般 背 ιέ 之 I 所 請 為 銑 m 之 鏑 造 物 切 削 屑 (生嫌屑) 用 作 為 廢 棄 物 拋 棄 、r- 刖 注 意 事 1 k 1. — 般 係 以 粉 碎 機 粉 碎 〇 在 粉 碎 時 即 有 部 份 的 石 墨 脫 m 而 吸 項 再 1 附 在 生 鐵 粉 之 表 面 Ο 因 此 推 想 此 生 鐵 粉 被 水 膜 包 覆 時 石 墨 本 頁 、-1 即 具 有 陽 槿 之 作 用 另 — 方 面 嫌 則 有 陽 極 之 作 用 9 在 如 A丄 刖 1 1 j 述 電 流 流 動 時 9 陽 m 上 將 溶 出 嫌 * 而 陰 極 上 則 發 生 脫 由 化 1 1 反 應 等 之 遢 原 反 應 0 上 述 合 金 亦 有 皤 檯 作 用 » 因 此 應 該 可 1 1 以 溶 出 合 金 〇 另 一 方 面 陰 極 則 發 生 脫 鹵 化 反 應 Ο 訂 1 此 外 » 在 进 原 力 較 金 屬 嫌 強 的 合 金 之 場 合 * 更 易 維 持 1 1 m 原 環 境 • 與 鹵 化 有 機 化 合 物 之 電 位 差 更 大 9 脫 _ 化 反 應 1 1 速 度 亦 更 快 〇 .J V 再 者 9 使 用 鎂 — 鎰 合 金 鋅 — 鋁 合 金 鋁 一 鋅 — 鈣 合 ί I 金 鋁 — 錫 合 金 等 合 金 時 * 可 能 因 氧 化 膜 或 腐 蝕 生 成 物 不 I i 附 著 在 金 属 表 面 » 或 者 因 附 著 但 生 成 之 膜 不 细 密 (無纯態 1 1 化 )Pfl礙反應, 不致產生由堪原反應降低接觸效率之問題, 1 1 因 此 淨 化 反 應 之 效 率 高 〇 1 1 本 發 明 實 施 樣 態 之 一 之 -W4- 刖 述 遒 原 劑 Μ 水 溶 性 化 合 物 為 1 I 佳 〇 與 添 加 粉 末 等 固 體 之 場 合 比 較 • 其 與 鹵 化 有 機 化 物 之 1 1 I 接 觸 效 率 會 有 突 飛 性 的 增 高 • 而 可 加 快 脫 鹵 化 反 應 0 又 , 1 1 I 水 溶 性 m 原 劑 因 可 滲 透 人 土 壤 等 之 中 , 使 用 注 井 即 可 將 m 1 1 15 本紙張尺度適用中國國家標準(CNS ) Α4規格(210Χ 297公釐) 3949 8 4386 2 1 A7 B7 好漓部中决標卑局貝J-消资合作私印髮 五、發明説明( 16 ) 1 1 原 m 注 人 » 因 此 不 須 物 理 之 挖 掘 混 合 作 業 〇 再 者 在 淨 化 搡 1 | 作 中 * 在 思 原 狀 態 不 安 定 的 場 含 > 亦 可 回 收 污 染 物 之 浸 1 I 出 液 9 再 添 加 水 溶 性 m 原 m 1 之 後 再 注 入 t 即 可 容 易 地 恢 諸 1 1 復 堪 原 狀 態 〇 先 閱 讀 1 1 水 溶 性 還 原 劑 有 有 機 酸 或 其 衍 生 物 次 磷 酸 或 其 衍 生 背 T& 之 注 意 事 物 或 硫 化 物 塩 0 有 機 酸 有 羧 酸 、 磺 酸 > 酚 或 其 衍 生 物 等 1 ^ j. 0 羧 酸 1 例 如 含 碳 原 子 數 1 〜2 0 * 且有羥基取代者之單羧 項 再 填 寫 本 頁 1 酸 \ 二 羧 酸 Ή 三 羧 酸 或 四 羧 酸 即 可 〇 具 體 之 » 甲 酸 | 乙 酸 、 擰 m 酸 草 m 對 苯 二 甲 酸 等 為 佳 > 特 別 Μ 樺 m 1 I 酸 草 酸 等 含 碳 原 子 之 2〜10之脂肪族二羧酸為佳。 I 1 I 酚 衍 生 物 以 聚 羥 芳 基 化 合 物 為 佳 〇 聚 羥 芳 基 化 合 物 指 1 1 由 2 個 以 上 羥 基 取 代 的 芳 基 化 合 物 9 芳 基 化 合 物 有 苯 、 萘 訂 m 等 0 萘 茚 之 類 形 成 m 合 m 者 亦 可 〇 聚 羥 芳 基 化 合 物 1 1 9 例 如 1 , 2 , 3 - 三 羥 基 笨 1 , 4- 雙 羥 基 笨 為 佳 0 此 處 1 1 1, 2 , 3- 二 羥 基 苯 亦 稱 為 焦 沒 食 子 酸 > 焦 掊 酚 〇 其 m 性 溶 液 與 氧 氣 反 應 而 生 成 氧 化 物 0 J T I 有 機 酸 衍 生 物 有 塩 m S 醢 胺 酸 酐 等 1 而 Μ 塩 為 佳 1 1 I 〇 至 於 逆 離 子 並 無 特 別 限 制 1 納 離 子 等 鹸 金 雇 離 子 鈣 離 1 1 I 子 等 m 土 類 金 靨 離 子 i 嫌 雕 子 s 鈦 離 子 等 過 渡 金 鼸 離 子 等 1 1 無 機 離 子 9 或 四 烷 基 数 離 子 等 有 機 離 子 亦 可 〇 ί 1 次 磷 酸 之 衍 生 物 有 塩 m 等 , 而 塩 為 佳 〇 至 於 逆 雕 1 1 子 並 無 特 別 限 制 r 納 離 子 等 m 金 羼 離 子 ,· 鋁 離 子 等 m 土 頬 1 I 金 羼 難 子 * 嫌 離 子 > 钛 m 子 等 通 渡 金 屬 雠 子 等 無 機 雛 子 » 1 I 或 四 烷 基 教 離 子 等 有 機 離 子 亦 可 0 1 1 本紙張尺度適用中國國家料(叫織格Ui⑽瓣楚) 39498 ^386 2 1 A7 B7 經淖部中决標準局負T;消费合作社印絮 五、發明説明(17 ) 1 I 前 述 逐 原 劑 為 有 機 酸 N 次 磷 酸 及 其 嫌 Λ 钛 鋅 > 錳 1 I 鋁 或 鎂 塩 均 可 0 1 1 I 添 加 此 m 原 劑 之 場 合 9 幾 乎 沒 有 —L 般 報 告 經 常 在 厭 氣 請 鬩 讀 1 1 I 性 脫 鹵 化 反 應 中 生 成 蓄 積 的 氯 化 乙 烯 等 中 間 代 謝 產 物 » 1 1 I 因 此 可 知 所 有 的 反 應 生 成 物 均 7ϋ 全 轉 變 為 脫 鹵 化 物 霣 而 釋 背 1¾ 之 出 於 氣 體 部 份 0 此 外 使 用 檷 準 電 極 電 位 與 金 靥 m 同 等 或 注 意 事 1 'j. 下 的 m 原 m 之 場 合 更 佳 參 因 為 與 鹵 化 有 m 化 合 物 之 罨 位 項 再 填 1 1 差 更 大 更 可 促 進 脫 鹵 化 反 應 0 m 原 劑 之 使 用 ft 在 污 染 物 寫 本 頁 、, V. I 為 土 壌 之 埸 合 * Μ 每 100g 土壤 0 . 01 20g為佳, 0 .05 〜1 0 g 1 1 I 更 佳 0 污 染 物 為 水 之 場 合 t Μ 每 100磁1水0 .1 3 0 g為佳, 1 1 I 0 . 2- -2 0g則 更 佳 0 但 不 論 何 種 場 合 9 在 脫 鹵 化 對 象 之 鹵 化 1 有 機 化 合 物 的 污 染 濟 度 在 超 通 50 1 g / kg(或 50® g/ 1 )之場 訂 合 » 有 必 要 對 每 1 Β g鹵化有機化物Μ 0 .0 5〜0 .1 g之比例壜 1 1 加 金 羼 粉 末 等 m 原 劑 之 添 加 量 0 但 此 终 究 係 理 想 條 件 下 之 1 [ 數 值 t 在 η 際 污 染 現 場 中 > 由 於 微 生 物 有 無 法 顚 利 地 消 耗 氧 氣 之 場 合 * 即 有 可 能 無 m 地 消 耗 堪 原 劑 之 堪 原 力 0 另 外 I I , 雨 水 或 大 氣 之 氧 氣 供 應 亦 可 容 易 地 消 耗 原 劑 之 适 原 力 1 1 > 因 此 必 須 先 於 實 m 之 規 場 進 行 月U 置 試 驗 f 決 定 合 於 規 1 1 場 條 件 之 各 添 加 濃 度 〇 i 1 為 提 高 思 原 劑 與 污 染 物 之 接 m 效 率 - m 原 劑 以 粉 末 狀 1 I 或 溶 液 為 佳 〇 但 上 述 物 質 往 往 易 於 與 水 反 應 而 變 為 氧 化 態 1 I * 因 此 此 種 場 合 ΡΛ 污 染 物 與 堪 原 劑 直 接 混 合 * 或 混 合 刖 再 1 1 I Μ 水 溶 解 為 佳 〇 1 1 P 在 通 原 爾 為 粉 末 狀 之 場 合 t 以 粒徑5 0 0 w β Μ 下 者 為 佳 1 1 17 本紙張尺度適用中國國家標準(CNS ) Λ4規格(210X297公1 > 3949 8 A7 經硪部中央標準局員工消費合作社印^· 4386 2 1 B7 五、發明说明(18 ) 。此乃因為粒徑小之場合,可Μ提高鹵化有攧化合物之分 解率。 此外,邐原劑視用途W粒徑0.001·»至5mB之粉末為佳 ,O.OlBiMliDin之粉末更佳。粒徑可影響化學性适原反應 之速度,因此須注意粒徑之增加脅成比例降低單位重量之 堪原反應速度。再者,粒徑在上時,因為金觸物質 之場合中金羼粒之表面會包覆較厚的氧化鹂之故,中央部 份理原狀態金雇可能無法被利用。此外,粒徑在O.OOlaa 以下之場合,由於氧化速度極為迅速,會增加運送中及混 合時與水接觸而氧化之危險性。在堪原劑為金屬物霣之場 合,因為粉末之表面氧化時,内部仍可能為缠原狀態,因 此須使其氧化才可以利用。 從雇營養型厭氣性微生物,例如:因甲烷生成细菌 (例如: Methanosarc inaS、 Methanothr ixB 、 MethanobacteriuiaB、Methanobrev iba^terM )硫酸運原 细菌(例如:DesulfovibrioM、Desulfotomac u Lujn B、 DesulfobacteriuaB 、 DesulfobacterU 、1T -.f Member of the Middle Standard Bureau of the Ministry of Economic Affairs, J. Consumer Cooperatives, the carbon state machine contains the use of China-Malaysia camps, so the state 3 % Of the amount of oxidized oxygen due to the production of loam, and the reaction of the thiologenic phase of microalcohols, such as odorous substances, odors, and odors, should be reversed. Yang Ying and 0 Yuan Shi will have the product of the 4th Mingfa in this special situation, because the mixture of the step is contaminated with the source to the highest M. The mixture can be evenly contaminated by the time.雅 : Upper M This paper size is applicable _: Standard (™ Specification U10X Supplement 3 9 498 43 86 2 1 A7 B7 in the Ministry of Economic Affairs " Printed by the Consumers' Cooperatives? The fifth, invention description (5) 1 and • The kangen agent used in the third aspect and the fourth aspect of the present invention > x 1 I The user in the first aspect or the second aspect of the present invention is preferred, but is not limited to 1 1 I using this Invention No. 1 The m original agent used in the aspect or the second aspect. 〇1 I Read 1 I The 1st aspect of the present invention is the purification method for halogenated organic compound pollutants. The first I 1 I method »The method provided is κ 25. For the standard electrode of the 檷% hydrogen electrode μ »Back 1 \ 13 m π 2 m original agent and 2 dependent anaerobic microorganisms Note 1 1 1 Ψ J < nutrient source is added to the aforementioned pollutants step «Its, A ·, and U. The original agent is m. The original item is 1 4 1. The percentage of ferrous metals is cut off — silicon alloy Λ titanium alloy \ zinc alloy manganese alloy, aluminum alloy | gold-magnesium alloy, calcium alloy, and water-soluble compounds In the group of groups, at least m is selected!! I 1 species 0 The existence of the m original agent »can promote chemical reactions and debiological binding 1! The dehalogenation of halogens 0 i 1 is described in the present invention m The original agent M sets the potential of the quasi-hydrogen electrode at 25 at a potential of "4 0 C bV -2400b V", and it is a reduction susceptor, osmium sulfide, and A * ti susceptor-Silicon 1 I gold-titanium alloy zinc alloy > At least one of the manganese alloy, aluminum alloy magnesium alloy, and calcium alloy 1 I is preferably selected thinly. 刖 mentioned kangen agent > λ containing kan original suspect is better 〇1 Λ.Λ * month [J It is better that the original agent also contains suspects. ^ U The original reason is also based on m — I silicon alloy Λ titanium — silicon alloy > titanium-aluminum alloy > zinc-aluminum alloy% manganese-magnesium 1 1 Alloy aluminum—zinc—calcium alloy—aluminum—tin alloy, aluminum—silicon alloy magnesium— 1 1 At least one selected from the group of manganese alloy and calcium—silicon alloy is preferred. 0 1 1 Preferably, the aforementioned m is m, which is an organic 1 1 acid or a derivative thereof, a hypophosphorous acid or a derivative thereof, or a sulfide, and is more preferably i 〇 »> Particles with a particle size of 5 0 0 ju η Μ are better. 0 The aforementioned contamination 1 1 1 is better if the moisture content is at least 25% by weight. 0 1 1 This paper size is in accordance with China National Standard (CNS) Α4 size (210 × 2). ? 7 mm) 5 3949 8 4386 2 1 Λ7 Α7 Β7 Seal of the Ministry of Economic Affairs, Ministry of Economy, Trade and Industry Bureau, Consumer Cooperatives ^ · V. Description of the Invention (6) 1 | M 1 1 I halogenated organic compounds dehydrohalogenated t The aforementioned pollutants have a pH of 1 in the range of 4.5 ^ -9.0 1 1 1 It is better to have the step 0 If the other steps after the aforementioned addition step to maintain the aforementioned stain 1 ! 诮 1 1 Dyestuffs are better in the original environment in the range of ρΗ4.5 ~ 9.0 0 Read II Read 1 I Describe dyestuffs M Add various kinds of stacks of organic matter m > Stacks have back 1¾ 1 Μ Organic matter, or waste water or waste containing organic matter, and If there are mixed steps, the book 1 \ I is better 0 项 item and then 11 1 1 In the first aspect of the present invention, the aforementioned water-soluble entrapment agent is 1 ~ 20 carbon 'Xing script £ 1 1 atom and hydroxyl substitution It is not possible to use carboxylic acid, dicarboxylic acid, tricarboxylic acid, 1 1 I or tetracarboxylic acid or its derivatives, polyhydroxyaryl compounds, or hypophosphorous acid or its phosphonium 1 1 is preferably 0. In addition, 9 the aforementioned water solubility Bulk agent 4 is preferably hypophosphorous acid or its phosphonium. 0 1 1 Describes the water-soluble entrapment agent organic acid or hypophosphorous acid or with iron \ 呔 \ zinc, manganese 1 or aluminum or magnesium. 0 1 1 is Adjust the pH of the »* -mentioned contaminants» Describe the contaminants M. It is better to add at least one of the alkali metal contacts 1 I compounds N alkaline earth metal compounds, and the steps are as follows. The step is to convert the halogenated organic compounds into halogen-free organic compounds. It is preferable that the above-mentioned holding step M can convert the above-mentioned toothed compound 1 1 to a hydrocarbon compound that does not contain a halogen atom. It is preferably 0 I i The second state of the present invention provides a purifying factor. Method for 1 compounds to cause 1 1 pollutants • Including the steps of reducing the 祢 standard electrode of 25 pairs of standard hydrogen electrodes to 1 1 position 130 η V ~ 2 4 0 0 1 V 剤 adding to the aforementioned pollutants, 1 I · »* -Describes that Kanhara is considered to be selected from the group consisting of Kanbara iron and Ni, a silicon alloy titanium alloy Λ zinc alloy 1 1 gold-manganese alloy aluminum alloy magnesium alloy, calcium alloy and water-soluble compounds At least 1 type 0 1 1 This paper size is applicable to Chinese National Standard (CNS) Α4 size (21 〇 × 297 mm) 6 3949 8 4386 2 1 A7 B7 Ministry of Economic Affairs " Standards Bureau member J · xiao fr Cooperatives printed five, Description of the invention (7) 1 I In the second step of the present invention, the former m agent M 25 V The standard electrode potential of the 檷 quasihydrogen 1 1 I electrode is -400 Β V -24001 V. It is entangled with the original, 1 1 and the cut off_ silicon alloy titanium alloy% zinc alloy manganese gold aluminum alloy m /-*, ii Please select at least one of the 1 alloy and calcium alloy is better. Read I i ύ i | The former reducing agent contains m original iron is better 0 > Better 0 The foregoing agents are iron-silicon alloy, titanium-silicon alloy titanium—m meaning 1 thing L alloy> zinc—aluminum alloy manganese—magnesium alloy S aluminum—zinc—calcium alloy% aluminum—item 1 4 1 tin alloy > Aluminium-silicon alloy, magnesium-manganese alloy, and calcium-silicon alloy group. At least one selected from the group I is more preferable. 0 Η 1 1 I The former transport agent is also a water-soluble compound. Buried raw m Μ has 榇 1 1 acid or its derivative> The hypophosphorous acid or its derivative or m compound is preferred 0 1 1 The aforementioned m original agent> X powder with a particle size of 5 0 0 // 〇Μ Order 1 for the best. The third aspect of the present invention is to provide a method for purifying the pollutants caused by halogenated hafnium compounds. The standard electrode contains 25 counter-electron quasi-hydrogen electrodes. The I position is 1 30 n. 2400 bV kangen agent, and the trophic anaerobic microbiotic 1 tt nutrient source added to the above mentioned pollutants »丄 刖 逑 nutrition source contains cl organic carbon and the aforementioned organic carbon 20 50 The oxidized state by weight% 〇 t 1 and t The aforementioned nutrient source contains 20 30% by weight of the above-mentioned oxygen-containing carbon 1 1 chemical nitrogen is more preferable. The organic carbon is used to supply a water-soluble fluorinated carbon source as佳 1 1 1 〇 Further »The standard of the standard argon electric hibiscus under the predetermined agent M 25 The electrode 1 1 I has a potential of -400 ancestor V " w -2400, V is preferably a metal substance. The aforementioned primogenizer K 1 | m is considered to be pig iron-silicon alloy, titanium alloy, zinc alloy, manganese alloy 1 1 and at least one of m in the group of aluminum alloy magnesium alloy and calcium alloy is better. National Standard (CNS) A4 specification (210X 297 mm) 7 3949 8 43 86 2 1 A7 B7 V. Description of the invention (8) Or, the aforementioned water-soluble compounds of kanji agents are also good. Powders of i D or less are preferred. The Ministry of Economic Affairs has determined that the standard of J-Consumer Cooperative Society shall be in accordance with the requirements of the J-Consumer Cooperative Society, and the addition and selection of fermentation and physical processes. Adding gold selection for the best-in-class bio-electricity step, the state and low He Jizhan's fan solution before. In the middle, add λ before the shape of the person, the nature of convergence 0 focus on the good titanium body Tim ^ = of the rri Mi wall 臛 _. The mixture of materials and gas is a plus, and there are many in the group Take it! One or calcium its. Halogenated hydrogen contamination P and the original silicon contamination have been added with aluminate or nitric acid, and are included in the entanglement | Calcium and added state nitric acid and nitric acid are classified as standard precursors. Nitrate or glutamate is mixed with the former wm, gold in wfl > step oxygen, potassium, containing the lower agent, and the contaminated parts will not be combined into 1 as a manganic acid. Powder and 50 mg of magnesium * Continued with the former auric acid nitrate which contains 25% of the former gas, the diameter, "II is more than that of koji nitrate, osmium, or. It is included with the regularizer to granulate the gold-cutting step. Nanometer liquid sample, liquid ην lower the original mixed CM original mixture ~ 1 add suspended nitric acid, waste state cultivation 00 Contained in the 遢 re-better agent Kalumi section 1, 3 containing acid nitrate source enzyme 4 Fang Ying 24 The description is the original M,.之 之 合 第 M Nitrocarbon-containing 酦 第 的 'Before the step, the internal compound Jin Jia 1 mixed with the amount of 塩, with 物 or the substance of water V mixed with the original compound as the first titanium titanate塩 有 、 明 染 and 01 are mixed with dyed and then mixed with manganese species, the dyes are nitric acid, and the source of pollution is described above. 13 mentioned before, the pollution is described as above. In this description, the former Jin Shao described the pollution before and the waste body camp. Suspected, Gu Zhidian-Step ahead of He Zinc (please read the precautions on the back before filling this page) This paper size applies to China National Standard (CNS) A4 size (210X297 mm) 8 3949 8 438621 A7 B7 恕 部 中 泱 支 Jujube Bureau Member-x Consumption Hezhusheyin 'f' 5. Description of the Invention (9) The step of nourishing fluid is better 0 1! Or »It is better to include the aforementioned pollutants in the first step Add 1! | Mix the aforementioned nutrient solution in the amount of 1 to 5% by volume of the stated pollutants, and then read 1 1 in step I 2 and add 1 to the stated pollutants and mix with the first phase First read 1 1 1 5 ~ 10% by volume of the previously mentioned nutrient solution, which is described as 1 J. The amount of pollutants mentioned above, and then add the above-mentioned JW ·· month U pollutants to the first stage or the second stage. At this stage, a larger amount of precautions 1 * 1, the previously filled liquid 0 items and then fill in 1 1 In addition, t describes the original agent M water-soluble compound 1 or Said the original agent is written on this page 1 It is better to dissolve in the aforementioned nutrient solution. Another 1 Λ. * · In the rest step t Λ, «· 刖, ^ 1 I The above-mentioned pollutants are at least the first 3 days. It is better to keep the inner M at 17 Q0V. 0 1 1 I In the fourth aspect of the present invention, the aforementioned nutrient solution 1 1 added to the r u- described contamination 1 > λ is finally 15 25% by volume of the aforementioned pollutant amount It ’s better. Also, > In the above-mentioned standing step »Keep the above 1 1 at least the first 5 days Contaminant at 17 60 Ό is better 0 In addition * In the above-mentioned standing step 1 Μ to 1 | Less in In the first 3 months, or preferably within 5 months, it is better to keep the aforementioned pollutants at 岫, 20 4〇υ 0 | The aforementioned standing step > λ and the surroundings are separated from each other and it is better to 0 to maintain 1 1 Low aeration conditions September IJ mentioned pollutants are best covered with non-aerated material 0 will be 1 1 It is also good to keep the pollutants in an aqueous liquid to maintain low aeration conditions. The above mentioned pollutants 1 1 are preferably mixed with the nutrient solution of A * month IJ in the container > >-the reducing agent is preferably 0 1 1 A simple explanation of the formula 1 The first picture shows the result of the test of the iodine detoxification reaction 1 1 I in which the four-gas ethylene-contaminated soil 1 I Μ for the production of tofu was tested under anaerobic conditions according to the present invention σ 1 1 This paper size applies Chinese national standard ((.: NS) Λ4 specification (2 丨 0 > < 297 gong)) 9 3 9 498 4386 2 1 A7 B7 The Ministry of Consumer Affairs and the Ministry of Standards and Decision Bureau have a negative T and eliminate cooperation印 印 5. Description of the invention (10) I The second figure shown in Fig. 2 is the soil contaminated with tetramethylene ethylene in accordance with the present invention. Fruit 〇 Reading Xian 1 i I a. Ming harm m Form 1 | Read 1 \ The 1st sample of the 2nd state of the present invention > and the 3rd state are cleaned by the halogenated back 1 hosiery compounds and pollutants. 0 Halogen refers to the atmosphere and the atmosphere in this manual V Note 1 *丨 _ Bromine N sulphur. The present invention can purify dyes containing halogen compounds with m compounds. 1 * Particularly, it can purify pollutants containing organic compounds containing chlorine and bromine atoms. Page V on this page is even more special. ≫ Pollutants with atomic compounds. This gasification is not limited to-1 I organic compounds. For example,-tetramethylene ethylene three gas ethylene 1, 1, dioxan 1 1 J aliphatic compounds such as ethanedichloroethylene, pentachloro. Aromatic compounds such as phenols 1 1 can also be decomposed. Order 1 The first aspect of the present invention, the second aspect, the third aspect, and the fourth aspect, which can be treated by I 1 include: soil, bad sediment, sludge Wait 〇 this Out of t compost 1 | compost m can be treated with methane m waste, etc. In addition »1st aspect of the invention Ί 2nd and 3rd aspects can also handle groundwater, m water and other water, Ί 1 property Liquids: The aqueous liquids in this description include: • Aqueous solutions \ suspensions 1 i 1% emulsions and mixtures thereof 0 1 1 Where the contaminant is soil, sediment, sludge, etc. 1 Water content M at least 1 1 Above 25% by weight, 40% by weight and 60% by weight are more preferable. 0 For breeding of anaerobes. 1 1 Sexual microorganisms ψ Soil sludge is not easily accessible by air. 1 I 〇 Water content (%) The definition is as follows: 01 I Moisture content = (Weight of water / Weight of pollutants of water content) X 100 1 1 1 W · When the pollutant is groundwater Λ m water, etc., the water content must be at 1! This paper size applies China National Standard ((.'NS) Α4 Specification (2f〇X297 mm) 10 3 9 498 Ministry of Labor " Printed by the Standards Bureau Employees' Cooperatives ^ 4 3 8 6 2 1 a? B7 V. Description of the invention (11) 25% by weight Μ. In the first aspect of the present invention, the aforementioned pollutant is added with a standard electrode potential of 130bV--2400η \ ί to a standard hydrogen electrode at 25T, and a nutrient source of anaerobic microorganisms derived from tritium, M promotes chemical reactions and biological reactions, and decomposes halogenated europium compounds. Where the potential of the quasi-electrode of the substance is higher than 130bV, sufficient reducing power cannot be obtained. On the other hand, the standard electrode potential of the substance is lower than -2400iV. For example: salty gold carvings such as gold tincture, gold tin potassium, etc., because the primordial force is too strong, it is prone to eruption in the presence of water and generate hydrogen. Dangerous and therefore inappropriate. The quasi-electrical potential (E °) of the standard hydrogen electrode below 25 is shown in the table below. (Please read the back of the page first, and pay attention to this page before filling in this page.) This paper size applies to the Chinese National Standard (CNS) A4 specification (210X297 mm) 39 498 438621 A7 B7 V. Description of the invention (12) Standard hydrogen electrode at 25C The quasi- 电位 potential (ε °) is printed by the iodine ministry standard standard bureau and consumer cooperation " '霣 hibin reaction E ° UV) Ca2 + + 2 & ~ < r Ca -286 5 Na + + e- < --> Na -2714 Hg2 + + 2e_ — 4 Mg-23 63 Al3 + 3e ~ <-> Al -1662 Z n 2 + 2e- ^ Zn -763 Fe ^ + + 2e-^-Fe -440 Cd2 + + 2e- <--> Cd -403 N i 2 + 2 e-f N i -250 Sn2 + + 2e ~ < r Sn -136 Fe3 + + 3e- <-— Fe -36 2H + + 2e '^-> H2 0 Ascorbic acid (pH7. 0) 58 (Please read the precautions on the back before filling out this page) '11 The potential of the quasi-electrode, that is, in the battery reaction, Each chemical species that reacts with the battery is under a pseudo-state (pure solid phase, pseudo-concentration, standard pressure, etc.), and the potential measured when the K-argon electrode is used for comparison electrode measurement is the pseudo-potential E. . This value can be expressed by the following formula. Ε ° ~-Δ G ° / nF where AG. For the response of the battery, Gibb's free energy changes, 12 paper sizes are in accordance with the Chinese National Standard (CNS) A4 (210X297 mm) 3 9 498 438621 A7 ____ B7 V. Description of the invention (丨 3) η is the reaction phase Number of electrons, F is Faraday constant. It must be noted that, in general, the oxidation potential is measured using a saturated silver nitride electrode as the comparison electrode. The measured value in this case is more than that shown in the measurement using the hydrogen quasi-electrode as the comparison electrode. The quasi-potential is about 200niV lower. In the present invention, the above-mentioned "primitive agent" is at least one selected from the group consisting of Tongyuangan, Shengyuan, Si-Si alloy, titanium alloy, zinc alloy, manganese alloy, aluminum alloy, magnesium alloy, aluminum alloy, and water-soluble compounds. For the aforementioned kangen agent, M is preferably applied to a standard hydrogen electrode at 251 (gold surface material with an electrode potential of _400nV to 2400biV). As one of the actual pickled forms of the present invention, the use of Shivagen is a rhenium agent, and the cut powder usually forms oxide scales due to surface oxidation. In contrast, the scale of Yunyuan 镪 (read the precautions on the back and then fill out this page) seeding * quantity purchase is good »use to Jianyi, with Hansi as a benefit? Ϊ Ke Zhigong can be reconstituted in the form of _. It is also considered to be limited. The original M miscellaneous form)). However, the content of the raw material can be reduced to the original β public oxygen, and the cut-off of the stock will be limited to the industry and the net cost will be higher. Oxygen content can also make Cheng Jia's chemical industry more pure and pure oxygen. It is called light-but it can be attributed to quality and medium-time debris. Fingers stand. Self-esteem is similar to suspicion of making a high, the last Communist Party can be like, raw powder, originalization: The principle is that the original will be aerobic, it will be aerobic and truthful, but it will also return to the finest example. He Yu-Shi, the Micro-Hydrogen limit its easy to confirm the extreme series. In addition, it is suspected that the tweezers of oxygen can be combined with the full cut, which will be easy, the classics will be safe, and the temperature will be warmed. One of the suspects is a high-oxygen 90 biofilm. Made. This paper size applies Chinese National Standard (CNS) A4 specifications (2) 0XW7 mm) 13 3 9498 438621 A7 B7 The final bid rate of the Ministry of Economic Affairs is negative T. Consumption Cooperation Private Printing 5. Inventory (14) 1 1 It becomes the iron for industrial use »The carbon m degree is about 2% (heavy director) M is 1 1 | m, and carbon containing in this M is called the birth m (" Physical and Chemical Dictionary "4th edition, II | 1 9 87 p. 411). The mechanical properties of steel are better.> Industrial products that can be processed and used as many as 1 1 1 are counted. 0 In exploring the use of cutting m chips to purify contamination caused by halogenated organic materials, please read I 1 1 compounds.% However, the oil back is used in the cutting process. Therefore, there is oil in the cuttings of steel products. Because of the use of the belly, it is necessary to pay attention to the organic atmosphere in the present invention. 1 ^ |. The method of purifying the pollutants caused by the compound may be caused by the oil 2 Sub-item again 1 [Pollution 0 Relatively 9 Razor made use of suspicion 1 Because the oil written on page I when cutting is not used »Do not worry about the cutting chips (raw rust) of m products as mentioned above mm 1 1 2 times contamination of I chippings 0 1 1 In other embodiments of the present invention, the alloy can be used as the original m 0 or 1 1 to use a silicon alloy, a titanium alloy, a zinc alloy, a manganese alloy, and an aluminum alloy. magnesium alloy Calcium alloy 0 Titanium alloy such as grain silicon alloy> Titanium—Aluminum 1! Alloy 〇Zinc alloy t such as zinc-aluminum alloy 〇Manganese alloy • For example: manganese—t | magnesium alloy 0 aluminum alloy * such as aluminum—zinc—calcium alloy aluminum — Tin alloys> 0 magnesium alloys such as aluminum-silicon alloys ♦ Example: Magnesium-manganese alloy ΰ Calcium alloy 1 case \} -1 I such as calcium-silicon alloy 〇1 1 Where the action of kangen agent can be reduced by the original source As an example to illustrate the reaction mechanism of the 1 J m gas dehalogenation reaction of metal susceptibility * The reaction of 遢 hara cutoff is based on the report of 1 1 (“Treatment of groundwater contaminated by organochlorine compounds-~ Μ 金 靥 搛 靥 搛 1 I activity Technology for the treatment of carbon at low temperature J PPH, 1995, Vol. 26, 1 I Page 5 虢 1 Page 64 70)), the adsorption of halogenated 1 I compounds will occur on the surface of Tanglehara E » Due to the difference between the original surface of the m and the environmental aspect of the m 1 1 I condition Polarization of anode and cathode occurs> Therefore, there will be a current pulsation 〇I 1 14 This paper size applies the Chinese National Standard (CNS) Λ4 specification (2) 0 × 297 mm 3 9 498 4 3 8 6 2 1 a7 B7 Warp ,% · Ministry " Yinjin Bureau Zhen-τ · Consumer Cooperative Press 5 、 Invention Note (I5) 1 I At the same time, m on the anode forms 1 ion dissolution f electrons are implanted on the anion m due to 1 I tt Halogenation reaction, etc. 1 Through the original reaction 0 1 1 I Yang plant: F e F e2 + + 2 e _ 谙 I 1 | Health m As mentioned above refers to the carbon concentration of 2% or more,-generally the weight first read ik 1 t [3 Λ -3 .596 »The capacity is graphite, which contains 13 -W 14% carbon with a large amount of carbon. The cutting chips (raw chips) of milled m are used as waste, r- 刖 Note 1 k 1. — Generally, it is pulverized by a pulverizer. During the pulverization, part of the graphite is removed, and the suction item is attached to the surface of the pig iron. It is inferred that when this pig iron powder is coated with water film, the graphite page, -1 has the function of hibiscus. The other is that it has the function of anode. 9 It will dissolve on 9 yang m when the current flows as described in A 丄 刖 1 1 j. I suspect that the dehydrogenation reaction occurs on the cathode 1 1 reactions such as 0. The above alloys also have a deuterium effect »so it should be able to dissolve the alloy 1 1 On the other hand, a dehalogenation reaction occurs on the cathode 0 Order 1 In addition» In the case of alloys with a stronger original force than metal *, it is easier to maintain the original environment of 1 1 m. • The potential difference with halogenated organic compounds is larger. 9 De_chemical reaction 1 1 The speed is also faster. 0. JV Furthermore 9 uses magnesium — 镒Zinc alloy—Aluminum alloy—Zinc—Calcium alloy I Gold-Aluminum—Tin alloy and other alloys * May be attached to metal surface due to oxide film or corrosion products »I may not be fine due to adhesion (No pure state 1 1) Pfl hinders the reaction and does not cause the problem of reducing the contact efficiency by the kangen reaction. 1 1 Therefore, the purification reaction has a high efficiency. 01 1 -W4- One of the aspects of the present invention Agent M Water-soluble compound is better than 1 I. Compared with the case where solids such as powder are added. • Its contact efficiency with 1 1 I of halogenated organic compounds will increase suddenly. • It will speed up the dehalogenation reaction. Due to its ability to penetrate into human soil, m 1 1 15 can be applied to the paper size using the Chinese standard (CNS) A4 specification (210 × 297 mm) 3949 8 4386 2 1 A7 B7 The Ministry of Justice and the Ministry of Justice decided to issue the J-consumer cooperation privately issued V. Invention Description (16) 1 1 Original m Note to people »Therefore, there is no need to physically dig for mixed operations. Unstable field in its original state Contains > Can also recover leaching of pollutants Add 9 water-soluble m to the original m 1 and then inject t to easily restore the original state. 1 Read 1 1 The water-soluble reducing agent is organic acid or its derivative hypophosphorous acid or its derivative. T & Cautions or sulfides 塩 0 Organic acids include carboxylic acids, sulfonic acids> phenols or their derivatives, etc. 1 ^ j. 0 carboxylic acids 1 such as monocarboxylic acids containing carbon atoms 1 to 2 0 * and hydroxyl substituted Please fill in this page again on page 1 acid \ dicarboxylic acid, tricarboxylic acid or tetracarboxylic acid. Specifically, formic acid | acetic acid, acetic acid, m-terephthalic acid, etc. are preferred > special M birch m 1 I acid An aliphatic dicarboxylic acid having 2 to 10 carbon atoms such as oxalic acid is preferred. I 1 I Phenol derivatives are preferably polyhydroxyaryl compounds. Polyhydroxyaryl compounds refer to 1 1 aryl compounds substituted with two or more hydroxyl groups. 9 Aryl compounds include benzene, naphthyl, etc. m and m can also be polyhydroxyaryl compounds 1 1 9 such as 1, 2, 3-trihydroxybenzyl 1, 4-dihydroxybenzyl is preferred 0 here 1 1 1,2,3-dihydroxybenzene is also known Pyrogallic acid > Pyrogallol. Its m-based solution reacts with oxygen to form oxides. 0 JTI organic acid derivatives are 塩 m S 醢 amino anhydride, etc. 1 and M 塩 is better 1 1 I 〇 As for the counter ion There are no special restrictions 1 ions such as nano ions, gold ion ions, calcium ion 1 1 I ions, etc. m earth ions ions i imitated s, ions, titanium ions, etc. transition gold ions, etc. 1 1 inorganic ions 9 or tetraalkyl ions, etc. organic Ions can also be derived from 次 m, etc. There is no particular limitation on the reverse engraving 1 1 ions, such as r nano ions, such as gold ions, · aluminum ions, etc. m soil I 1 I gold ions, etc. * ions > titanium m Hatchling »1 I or organic ions such as tetraalkyl ions can also be used 0 1 1 This paper size applies to Chinese national materials (called Zhige Ui ⑽ Chu Chu) 39498 ^ 386 2 1 A7 B7 Ministry of Economy and Trade Standards, negative T; consumption Cooperative cooperative printing V. Description of the invention (17) 1 I The aforementioned original agent is organic acid N hypophosphorous acid and its Λ titanium zinc > manganese 1 I can be aluminum or magnesium hafnium 0 1 1 I When this original agent is added 9 Few—L-like reports often read in anaerobic. 1 1 I Intermediate metabolites such as vinyl chloride accumulate during the dehalogenation reaction »1 1 I Therefore, we can know that all reaction products are 7ϋ fully converted to dehalogenation Releasing things 1¾ out of gas part 0 In addition Use quasi-electrode potential equal to gold 靥 m or pay attention to the case of m under 1 'j. It is better to use ginseng because the 罨 position term of the compound with halogenated m is further filled with 1 1 and the difference is larger, which can promote dehalogenation reaction. 0 m The use of the original agent ft On the page of the pollutant, V. I is the combination of soil ** Μ per 100g of soil 0.01 0g is better, 0. 05 ~ 1 0 g 1 1 I is better 0 pollutant In the case of water, t Μ is preferably 0.10 g of water per 100 magnets, 1 1 I 0. 2-2 0 g is more preferable 0, but in any case 9 in the halogenated object of dehalogenation 1 of organic compounds Pollution degree fit in the field of 50 1 g / kg (or 50® g / 1) »It is necessary to add a ratio of 0.5 to 0.1 g per 1 B g of halogenated organic compound 壜 1 1 plus The amount of m original agent such as gold tincture powder is 0, but this is 1 under ideal conditions [the value of t in the η pollution site> where the microorganisms ca n’t consume oxygen wisely * The original force 0 of the original agent is consumed in addition to m. In addition, the suitable original force of the original agent can be easily consumed by the supply of oxygen in the rain or the atmosphere 1 1 > Therefore, a monthly U test must be performed before the actual field of m. Determine the concentration of each additive in accordance with the conditions of the field of the 11 1 o 1 to increase the efficiency of the original agent and pollutants m-The original agent is preferably a powder 1 I or a solution. However, the above substances tend to react with water easily. It becomes an oxidation state of 1 I * Therefore, in this case, the PΛ pollutant is directly mixed with the kanji agent * or mixed, and then 1 1 I Μ water is better to dissolve. 0 1 1 P In the case of Tongyuaner powder, t particle size 5 0 0 w β Μ The lower one is better 1 1 17 This paper size applies Chinese National Standard (CNS) Λ4 specification (210X297 male 1 > 3949 8 A7 Printed by the Consumers' Cooperative of the Central Bureau of Standards of the Ministry of Economic Affairs ^ 4386 2 1 B7 5. Description of the invention (18). This is because when the particle diameter is small, the resolution of the halogenated europium compound can be improved. In addition, the rhenium agent is preferably a powder having a particle size of 0.001 · »to 5 mB depending on the application, and a powder of O.OlBiMliDin is more preferable. The particle size can affect the speed of the chemical adaptation reaction. Therefore, it is necessary to pay attention to the increase of the particle size to reduce the kanyuan reaction rate per unit weight. In addition, when the particle size is above, the surface of the gold particles in the case of gold-contacting materials will be covered with a thicker layer of thorium oxide, so the central part of the gold particles may not be used. In addition, when the particle size is less than OOlaa, the oxidation speed is extremely fast, which increases the risk of oxidation by contact with water during transportation and mixing. In the case where the original agent is a metallic substance, because the surface of the powder may be entangled when the surface is oxidized, it must be oxidized before it can be used. Employ vegetative anaerobic microorganisms, for example: methanogenic bacteria (for example: Methanosarc inaS, Methanothr ixB, MethanobacteriuiaB, Methanobrev iba ^ terM) sulfate transport bacteria (for example: DesulfovibrioM, Desulfotomac u Lujn B, DesulfobacteriuaB, DesulfobacterU

Desulfococcuss属)、酸生成细菌 (例如:ClostridiufflB、Acetivibnio臞)、B a ct&_r o i d e s 麗 Ruminococcus匾)、兼性顧氣性细菌(例如:B a c i 1 1 n sJI、 Lactobaci1lusB 、 AeromonasB 、 Streptococcus臛、 MicrococcusBi )等 〇 又,B a c i 1 1 a s Μ、PseudononasM、Aeromonas臞、Desulfococcuss), acid-producing bacteria (for example: ClostridiufflB, Acetivibnio 、), B a ct & _rooides Ruminococcus plaque), facultative bacteria (for example: B aci 1 1 n sJI, Lactobaci1lusB, AeromonasB, Streptococcus 臛, Micrococcus Bi), etc., and B aci 1 1 as Μ, PseudononasM, Aeromonas 臞,

Streptococcus題、HicrococcusB具有氧化態氮堪原活性 本紙張尺度適用中國國家標準(CMS ) Λ4規格(2】0X297公釐) 18 39498 (請先閲讀背而之注意事項再填寫本頁)Streptococcus, HicrococcusB has oxidation state nitrogen kanyuan activity The paper size is applicable to Chinese National Standard (CMS) Λ4 specification (2) 0X297 mm 18 39498 (Please read the precautions before filling this page)

438621 A7 B7 經湞部中决標準局負Jr消费合作私印$ί 五、' 發明説明( 19 ) 1 I 較 佳 0 1 I 從 屬 營 着 型 厭 氣 性 微 生 物 之 m 着 源 » 視 污 染 物 中 微 生 1 1 i 物 之 特 性 可 選 擇 缠 宜 者 0 例 如 可 g 甲 惊 生 成 微 生 物 培 養 基 r—'、 請 1 1 I > m 酸 堪 原 微 生 物 培 養 基 > 硝 酸 m 原 撤 生 物 培 養 基 等 中 番 A 間 讀 1 1 擇 任 一 種 9 邐 擇 時 可 先 以 淨 化 處 理 能 力 試 驗 (淨化遘用性 背 ΐέ 之 試 驗 )測定對鹵化有機化合物之淨化效率再決定。 ί 事 1 1. 甲 烷 生 成 微 生 物 之 曾 巷 源 9 一 般 所 知 之 甲 烷 生 成 微 生 項 再 1 ] 物 代 表 性 生 長 營 着 灌 的 乳 酸 甲 酵 N 乙 醇 乙 酸 捭 攆 酸 % 本 頁 V I > 丙 酮 酸 聚 蛋 白 腺 等 營 養 素 均 可 〇 又 » 臃 酸 适 原 微 生 物 1 I 之 生 長 彗 養 源 f 則 m 酸 m 原 微 生 物 生 長 營 養 源 代 表 之 乳 酸 1 1 I 甲 醇 乙 酵 > 乙 酸 擰 攆 酸 N 丙 m 酸 、 聚 蛋 白 諫 含 耱 L 1 訂 有 櫬 物 等 —* 般 所 知 之 營 着 素 均 可 〇 有 櫬 甲 烷 m 酵 處 理 對 象 之 有 機 性 廢 水 、 m 棄 物 ♦ 例 如 1 1 啤 酒 m 造 磨 水 m 粉 廢 水 酪 農 m 水 * 製 糖 m 水 或 啤 酒 1 1 酒 粕 豆 渣 污 ΑΕ3 m 等 較 有 效 果 » 可 作 為 從 屬 曾 養 型 厭 氣 性 微 生 物 之 生 長 曾 養 源 0 / I 添 加 液 體 撖 生 物 培 養 基 時 9 添 加 量 過 多 時 » 可 能 使 鹵 1 1 I 化 有 機 化 合 物 滲 透 人 地 下 而 擴 敗 污 染 » 相 反 地 t 通 少 時 無 1 1 法 保 持 微 生 物 生 長 之 缠 當 含 水 量 而 將 抑 制 生 長 〇 因 此 1 土 1 1 堳 中 水 份 含 量 (污泥等Μ 土壤為基準) 以 添 加 液 體 之 微 生 物 1 1 培 養 基 調 整 為 25 60% 為 宜 而 以 35 60% 為 佳 〇 關 於 培 I ! 養 基 之 添 加 里 9 必 須 充 份 考 處 土 壤 含 水 率 空 隙 率 粒 度 I 組 成 透 水 係 數 等 再 決 定 0 因 此 用 Μ 添 加 的 微 生 物 培 養 1 1 | 基 之 濃 度 t 視 污 染 土 壤 之 狀 態 , 其 培 養 基 量 各 有 不 同 • 須 1 1 本紙乐尺度適用中國國家標隼(CNS } Α4規格Γ210Χ 297公釐) 19 39498 43 86 2 1 at B7 經消部中决標準局員工消費合作社印^ 五、 發明説明(20 ) 1 | 慎 重 經 淨 化 處 理 能 力 試 驗 後 再 決 定 〇 1 1 此 外 , 土 壤 中 水 份 含 量 之 安 定 保 持 » 缠 當 混 合 矽 m 土 1 1 I 或 各 種 保 水 材 料 Ν 腐 植 土 等 即 有 效 果 〇 ^_____ 1 I 請 I 在 污 染 物 為 粘 土 質 土 壤 或 结 塊 之 粉 土 質 等 低 透 水 性 物 先 閲 1 I 讀 1 I 質 之 場 合 * 僅 使 用 缠 原 m 脫 氱 處 理 時 接 觸 效 率 低 > 須 要 長 背 ιέ 之 1 的 時 間 » 因 此 外 界 氧 化 物 供 給 條 件 將 可 能 引 起 還 原 狀 態 注 意 ! 事 之 不 安 定 0 此 種 埸 , 可 在 m 原 劑 之 外 再 添 加 微 生 物 生 長 項 1 填 1 基 質 之 有 櫬 碳 源 使 其 在 中 性 條 件 下 分 解 淨 化 而 安 定 通 原 寫 本 百 1 狀 態 , 達 到 完 全 脫 鹵 化 之 淨 化 〇 η '· 1 1 1 本 發 明 中 添 加 還 原 劑 後 , Μ 維 持 刖 逑 污 染 物 在 堪 原 環 1 1 境 中 為 佳 〇 在 此 之 還 原 環 境 例 如 以 水 等 斷 絕 空 氣 中 之 氧 L 1 氣 〇 由 於 從 属 營 蕃 型 厭 氣 性 微 生 物 興 分 解 有 闞 » 在 有 氧 氣 訂 等 時 將 抑 制 澈 生 物 之 生 長 0 m 原 劑 之 氧 化 亦 容 易 達 到 m 原 1 1 之 環 境 0 又 參 里 原 劑 消 耗 殆 淨 之 場 合 , 亦 有 維 Μ 保 持 埵 原 1 1 環 境 之 場 合 0 此 遇 原 環 境 以 25 下 對 檷 準 氫 電 極 之 標 準 電 極 電 位 為 (j 1 + 200 "2400m V範圍為佳, + 2 0 0 〜- 1000 it V 範 圍 更 佳 % + 100 1 1 -600 mV 範 画 又 更 佳 0 1 1 本 發 明 中 逐 原 性 眹 鹵 化 反 應 進 行 中 9 Μ 保 持 所 定 之 pH 1 1 為 佳 〇 具 體 α 之 * 即 Μ PH5 . 8〜8 • 5為 佳 * ρ Η 6 〜8 更佳, 1 I PH6 . 2〜7 • 6又 更 佳 0 如 此 9 在 安 定 地 保 持 特 定 之 pH及 厭 氣 1 I 性 環 境 之 場 合 * 即 可 Μ 保 持 邐 原 劑 表 面 上 的 有 櫬 化 合 物 有 1 1 高 脫 鹵 化 活 性 0 1 1 同 時 » 亦 可 Μ 預 先 添 加 pH 調 節 劑 在 污 染 物 中 0 該 pH 調 1 1 本紙張尺度適用中國國家標準(CNS ) Λ4規格(2!0X297公釐) 20 3 9 49 8 A7 438621 B7 五、發明説明(21 ) (請先閱讀背面之注意事項再填寫本頁) 節雜,在酸性土壤之場合,Μ使用_t金屬化合物或醮金土 類金羼化合物為佳,具體言之,可Κ使用一般無櫬系土壤 改良材料。例如:石灰石、生石灰、消石灰、磙酸鈣(石 資)、氧化鎂、岩土、真珠岩、沸石等。 再者,在處理時反應之進行上,添加各種堆脃、堆β 化有檐物等棍合更佳。主要因為已知此為長久以來的有機 系土壤改良材料,具有添加微生物效果及供給撤生物營養 源,保持水份之作用。 此有微生物曾着源及维持厭氣瑁境之作用,同時並有 分解、除去土壤厭氣醱酵時同時產生之惡臭氣體,尤其是 Μ硫化氫及甲基碕酵為首之碕磺系惡臭氣«之作用。 且,一般已知在各種堆肥中含有以放線菌、细菌為首 之各種微生物,其中存在多種可有效分解硫磺系惡臭物質 之微生物,因此可以容易地推測自各種堆肥中可以分離多 種有用的除奥微生物,並可利用堆肥作為除去家畜糞尿處 理中惡臭之對策。 經漓部中央標隼局員-Τ-消贽合作社印狀 依前述條件中,土壤中在添加驗金屬化合物、《I 土類 金饜化合物之類無機質系物質(多被稱之為無機質系土壤 改良材料)pH調節劑、有櫬質糸物霣(有機質系土壤改良材 料類)、及微生物培養基後,土埔中存在的厭氣性微生物 迅即開始生長,土壤中快速形成中性,厭氣性之環境,在 本發明中擔負化學性脫鹵化反應之埋原_琨合人土壤之時 櫬,在添加無機質系物質、有機霣系物質、撤生物培着基 時同時混合不但無任何不妥,甚至同時混合更有助於保持 本紙張尺度適用中國國家標準(CNS ) A4規格(210X 297公釐) 21 39498 A7 438621 87 五、發明説明(22 ) 長期之厭氣環境,且成本低廉,有利於污染淨化程序之管 理。 本發明之還原性脫鹵化反應應用於實際的污染地區時 ,並不需要大規棋設備之建設,只要在對象之污染土塯中 混合各種土壤改良材料及還原劑,再添加微生物生畏培着 基,同時在淨化區域覆K聚氯乙烯塑謬布等Μ達防止水份 蒸散及南水混入、保溫之目的即足夠。此外,為防止惡奥 氣鼸之發生,同時抑制水份之蒸敢,最好視需要在淨化地 區之土壤表曆鋪Μ腐葉土或堆肥。 本發明之堪原性脫鹵化反應之反應檐制中,目前仍有 未完全明瞭之處,本發明人等認為係如以下的情形。首先 ,保持土壤等污染物在ΡΗ4.5〜9.0,且維持厭氣環境下其 25t下對禰$氫罨極之播準電極電位在+200〜- 2400«V範 圍,並在土壤中添加無機質系物質及有櫬霣系物質以及微 生物培養基之微生物活化劑,將有利於營造厭氣性環境以 利用土壤中徹生物之生長反應。此場合中因為厭氣性撤生 物在土壤中快速生長,幾乎不會抑制化學性脫鹵化反懕, 因此生物性脫鹵化反應與化學性脫鹵化反應幾乎同時開始 〇 生物性厭氣脫鹵化反應之櫬制的撤生物學、酵素反應 學並未經極榭底的研究,因此仍未明瞭,但由厭氣性環境 下甲烷生成撖生物及确酸埋原微生物等偏性厭氣性微生物 及各種厭氣污泥、底泥中厭氣性激生物在生長狀態之場合 ,可檯為嫌慢的微生物反應一次一個氣地進行脫氛之 (請先閱讀背面之注意事項再填寫本頁)438621 A7 B7 The Ministry of Economic Affairs and the Ministry of Justice Standards Bureau Jr Consumption Cooperation Private Printing $ ί 5. Description of the Invention (19) 1 I better 0 1 I Dependent on the type of anaerobic microorganisms, the source of the epidemic »in the pollutants The characteristics of the microbiotic 1 1 i substance can be selected as appropriate. For example, g can be used to form a microbial culture medium r— ', please 1 1 I > m acidic bacterial medium > nitric acid m original biological medium, etc. Interim reading 1 1 Choose any one. 9 When you choose, you can first determine the purification efficiency of halogenated organic compounds by using the purification treatment capability test (purification test). ί Event 1 1. Zeng Xiangyuan of Methanogenic Microbes 9 Commonly Known Methanogenic Microbiotics 1] Representative growth of lactic acid formase N ethanol acetate acetic acid% of this page VI > Pyruvate Polyprotein glands and other nutrients are available. Also, the growth source of phytoplankton microorganism 1 I is the co-culture source f. M acid m lactic acid represented by the growth source of probiotic microorganism 1 1 I methanol acetic acid > acetic acid N propyl m Acids, polyproteins, 耱, L1, 榇, etc. — * Commonly known ingredients are available. 榇 Methane, methane, organic waste water for fermentation treatment, m waste, such as 1 1 beer m grinding water m powder wastewater dairy farming m water * sugar m water or beer 1 1 distiller's meal bean dregs staining ΑΕ3 m and other more effective »can be used as the growth of the affiliated anaerobic anaerobic microorganisms When liquid 撖 biological culture medium 9 is added too much »May cause halogenated 1 1 I organic compounds to penetrate the ground and expand pollution» Conversely, when t is small, there is no 1 1 method to maintain the entanglement of microbial growth When the water content will inhibit growth 〇So 1 soil 1 1 堳 The water content (soil and other soils as the basis) The liquid-added microorganism 1 1 medium is preferably adjusted to 25 60% and preferably 35 60%. Addition 9 must fully consider the soil moisture content, porosity, particle size, composition, permeability coefficient, etc., and then determine 0. Therefore, the microorganisms added with M are cultured 1 1 | the concentration of the substrate t depends on the state of the contaminated soil, and the amount of the medium varies. 1 1 This paper music scale is applicable to the Chinese national standard (CNS} Α4 size Γ210 × 297 mm) 19 39498 43 86 2 1 at B7 Printed by the Consumers' Cooperatives of the Bureau of Decision and Standards of the Ministry of Consumer Affairs ^ V. Description of the invention (20) 1 | Prudence Jingjing Determined after the treatment capacity test. 〇1 1 In addition, the stability of the water content in the soil is maintained »mixed with silica m soil 1 1 I or various water-retaining materials N humus soil, etc. have an effect 〇 ^ _____ 1 I Please I For clay-like soil or agglomerated silty soil and other low-permeability materials, please read 1 I Read 1 I for high-quality occasions * Only use entangled m for low contact efficiency when descaling treatment> It takes a long period of time to carry out »Therefore The external oxide supply conditions may cause the reduction state to pay attention! Instability 0 This kind of plutonium can be supplemented with the microbial growth item in addition to the original agent 1 Fill 1 The substrate has a carbon source to decompose under neutral conditions Purify and stabilize the original manuscript in the state of one hundred and one, and achieve complete dehalogenation purification. η '· 1 1 1 After the reducing agent is added in the present invention, it is better for M to maintain the radon contamination in the environment of Kanbara 1 1 0. The reducing environment here is to cut off the oxygen L 1 gas in the air, such as water. The subordinate anaerobic anaerobic microorganisms are decomposed and decomposed. »When oxygen is used, the growth of chlorophyte will be inhibited. 0 m The oxidation of the original agent is easy to reach m. The original 1 1 environment 0. On occasions, there are also cases where the dimensionality is maintained by the 埵 hara 1 1 environment. 0 In this case, the standard electrode potential of the quasi-hydrogen electrode at 25 times the original environment is (j 1 + 200 " 2400m V range is better, + 2 0 0 ~-1000 it V range is better% + 100 1 1 -600 mV range picture is even better 0 1 1 In the present invention, the original halogenated halogenation reaction is in progress 9 Μ Maintaining the predetermined pH 1 1 is good. Specific α of * That is, M PH5. 8 ~ 8 • 5 is better * ρ Η 6 ~ 8 is better, 1 I PH6. 2 ~ 7 • 6 is even better 0 So 9 In the stable environment to maintain a specific pH and anaerobic 1 I in the environment of the environment * can be maintained M on the surface of the primogenizer compounds 1 1 Halogenation activity 0 1 1 At the same time »It is also possible to pre-add a pH adjuster in the pollutants 0 The pH is adjusted 1 1 This paper size is applicable to the Chinese National Standard (CNS) Λ4 size (2! 0X297 mm) 20 3 9 49 8 A7 438621 B7 V. Description of the invention (21) (Please read the notes on the back before filling in this page.) In the case of acid soil, it is better to use _t metal compound or gold-earth metal gold-earth compound, specifically In other words, it is possible to use general soilless material for soil improvement. For example: limestone, quick lime, slaked lime, calcium osmate (stone), magnesia, geotechnical, perlite, zeolite, etc. In addition, in the progress of the reaction during the treatment, it is better to add various piles, piles, and β-eaves. This is mainly because it is known as a long-lasting organic soil improvement material, which has the effect of adding microorganisms, supplying nutrient sources for removing organisms, and maintaining water. This microorganism has the function of originating and maintaining the anaerobic environment, and at the same time, it also decomposes and removes the odorous gases that are produced at the same time when the anaerobic fermentation of soil is destroyed, especially the sulfonium-based odor gas led by M hydrogen sulfide and methyl hydration. The role of «. In addition, it is generally known that various composts include various microorganisms such as actinomycetes and bacteria. Among them, there are many microorganisms that can effectively decompose sulfur-type malodorous substances. Therefore, it is easy to speculate that a variety of useful microorganisms can be separated from various composts. And, compost can be used as a countermeasure for removing malodor in livestock manure treatment. According to the conditions of the Ministry of Central Standards Administration of the Ministry of Standards-T-elimination cooperatives, according to the aforementioned conditions, the soil is added with an inorganic substance such as a metal test compound and an "I soil gold compound" (mostly referred to as an inorganic soil improvement). Materials) After pH regulators, phytoplankton (organic matter-based soil improvement materials), and microbial culture media, the anaerobic microorganisms in the soil immediately began to grow, and the soil quickly formed neutral, anaerobic The environment, which is the buried source of the chemical dehalogenation reaction in the present invention _ when it is combined with human soil, when adding inorganic substances, organic actinides, and bio-implantation substrates, mixing at the same time is not without any trouble, even At the same time, it is more helpful to keep the paper size applicable to the Chinese National Standard (CNS) A4 specification (210X 297 mm) 21 39498 A7 438621 87 V. Description of the invention (22) Long-term anaerobic environment, and the cost is low, which is conducive to pollution Management of purification procedures. When the reductive dehalogenation reaction of the present invention is applied to an actual contaminated area, no construction of large-scale equipment is required, as long as various soil improving materials and reducing agents are mixed in the contaminated soil of the subject, and then microorganisms are added to cultivate the substrate. At the same time, it is enough to cover the purification area with K polyvinyl chloride plastic cloth and other M to prevent water evapotranspiration and the mixing of South water and keep warm. In addition, in order to prevent the occurrence of catastrophic obesity and suppress the evaporation of water, it is best to spread mulched leaf soil or compost on the soil surface of the purification area as needed. In the reaction eaves system of the degenerative dehalogenation reaction of the present invention, there is still not fully understood at present, and the present inventors believe that it is as follows. First, keep the soil and other pollutants at pH 4.5 to 9.0, and maintain the potential of the quasi-electrode at 25t under the anaerobic environment at +200 to-2400 «V, and add inorganic substances to the soil Microbial activators based on systemic substances and actinides and microbial culture media will help create an anaerobic environment to take advantage of the growth response of the organisms in the soil. In this case, because the anaerobic withering organisms grow rapidly in the soil, the chemical dehalogenation reaction will hardly be inhibited. Therefore, the biological dehalogenation reaction and the chemical dehalogenation reaction begin almost simultaneously. The biology and enzyme responsiveness of the control system have not been studied by the researchers, so it is still unclear, but the anaerobic microorganisms such as methanogenesis organisms and acid-protozoic microorganisms and various species in the anaerobic environment are still unknown. In the case of anaerobic sludge and bottom mud, when anaerobic excitants are growing, they can be deaerated one at a time for the slow microorganism reaction (please read the precautions on the back before filling this page)

.IV 經墒部中央標準局貝Η消費合作杜印t 本紙張尺度適用中國國家標隼(CNS )A4規格(210X29·/公釐) 22 39 498 43862 1 B; 經浸部中次標準局U貝-"消贽合作社印裝 五、發明説明( 23 ) ί 1 報 告 加 K 推 想 » 本 發 明 中 應 該 進 行 同 樣 之 媛 慢 的 m 原 性 脫 1 1 鹵 化 反 應 〇 1 | 本 發 明 中 淨 化 開 始 後 1 m 月 之 反 應 初 期 * 化 學 性 脫 1 1 先 1 鹵 化 反 m 應 占 大 部 份 • 之 後 随 著 鹵 化 有 櫬 化 合 物 污 染 濃 度 閲 1 降 低 及 通 原 劑 之 m 原 活 性 降 低 ♦ 化 學 性 脫 鹵 化 反 應 減 少 * 面 > 注 I 相 對 地 生 物 性 脫 處 化 反 應 漸 成 優 勢 > 但 脫 氯 則 長 期 間 直 意 事 j. 進 行 著 〇 此 生 物 性 脫 鹵 化 反 應 開 始 作 用 之 時 鹵 化 有 拥 化 項 再 填 1 合 物 污 染 之 濃 度 已 相 當 降 低 1 不 致 成 為 生 物 脫 鹵 化 反 應 之 寫 本 頁 V 1 濃 度 陣 礙 r 反 而 成 為 生 物 反 應 最 可 發 揮 之 低 m 度 污 染 1 脫 、_>-· 1 I 鹵 化 反 懕 作 用 應 更 為 活 躍 0 因 此 * 本 發 明 之 因 鹵 化 有 槺 化 I 1 1 合 物 污 染 之 淨 化 作 用 中 » 由 化 學 性 脫 鹵 化 反 應 與 生 物 性 脫 1 1 訂 1 齒 化 反 應 相 互 之 作 用 可 以 淨 化 至 極 低 之 濃 度 〇 本 發 明 之 化 學 性 及 生 物 性 鱖 氣 脫 氣 方 法 » 结 合 低 溶 解 1 1 性 土 壤 改 良 劑 類 無 機 質 % 物 質 及 有 機 質 系 物 質 , 不 僅 不 會 1 1 使 鹵 化 有 機 化 合 物 白 該 污 染 土 墉 中 溶 出 » 且 因 遘 度 保 持 該 污 染 土 壤 之 保 水 性 而 不 致 使 該 鹵 化 有 機 化 合 物 污 染 再 滲 透 1 I 入 污 染 位 置 Μ 下 之 深 層 地 底 * 因 此 > 可 Μ 短 期 間 低 廉 且 J 1 I 簡 便 地 淨 化 該 鹵 化 有 機 化 合 物 汙 染 土 壤 〇 1 1 本 發 明 之 反 應 * 可 以 一 直 進 行 至 W. 月 述 脫 氯 反 應 完 全 * 1 1 得 到 主 要 為 不 含 氯 有 機 化 合 物 之 產 物 而 此 為 含 鹵 化 有 機 1 1 化 合 物 污 染 物 充 份 淨 化 之 最 佳 情 形 〇 例 如 四 氯 乙 烯 及 二 1 1 氣 乙 烯 污 染 物 之 淨 化 * 主 要 的 產 物 為 TC 全 不 含 氯 之 乙 烯 > 1 j 乙 焼 有 機 化 合 物 1 此 反 應 中 幾 乎 不 產 生 含 氛 之 有 害 中 間 產 1 I 物 1 可 Μ 得 到 極 佳 的 結 果 〇 1 1 本紙張尺度谪用中國國家標準(CNS ) Λ4規格(210X297公犛) 23 39498 438621 A7 B7 五、發明説明(24 ) 本發明之第2態樣中,可Μ使用本發明第1態樣中使 用之堪原劑。即使不添加特定的營着源、亦無生物反懕參 與的場合,亦可以分解鹵化化合物。 以下說明本發明第3態揉及第4態樣中使用的遒原劑 。本發明之第3態樣及第4態樣中,可Κ使用在25t下對 搮準氫電極之標準電極電位為130nV〜- 2400mV之适原劑。 最好使用本發明之第1態樣或第2態樣中使用的還原劑。 但本發明之第3態樣及第4態樣中使用的遢原劑,並 不限於本發明第1 *1樣及第2態樣中使用的通原劑,可以 使用如:嫌(不限缠原鐵、生嫌)、錳、鎳、鎂、銅。金屬 嫌及金鼸錳因為天然土壤中即以氧化狀態大量存在,即使 * 添加對生態系之影響亦小,因此是安全的。此外,因為有 販賣因此易於取得。該遢原覿之使用量如上述即可〇 本發明第3態樣及第4態樣使用的堪原劑,以在25υ 下對標準氫電極之檷準電極罨位為-400bV〜- 2400bV之金 羼物質為佳。前述遢原劑Μ适原薄I、生锇、嫌-矽合金、 鈦合金、鋅合金、錳合金、鋁合金、鎂合金及鈣合金之群 體中選擇至少1種為佳。 此外,前述運原劑亦Μ水溶性化合物為佳〇前述運原 劑亦Μ粒徑500w βΚ下的粉末為佳。 以下以本發明第3態樣為主說明。與本發明第1態樣 共同之處則省略說明。 本發明第3態樣中,含將25C對檷準氫電極之檁準電 極罨位為130nV--2400iaV的運原劑及從屬營着型厭氣性撤 (請先閱讀背面之注意事項再填寫本頁).IV The Central Bureau of Standards of the Ministry of Economic Affairs of the People ’s Republic of China is responsible for cooperating with consumers. The paper size is applicable to the Chinese National Standard (CNS) A4 (210X29 · / mm) 22 39 498 43862 1 B; Shell- " Printing Cooperative Co., Ltd. V. Description of the Invention (23) ί 1 Report plus K Reasoning »In the present invention, the same slow m original desulfurization 1 1 halogenation reaction should be performed 〇1 | After purification starts in the present invention Initial reaction time of 1 m month * Chemical demineralization 1 1 1 Most of halogenated anti-m occupies the majority • Later, as the halogenated hafnium compound contamination concentration decreases, the original activity of the original agent m is reduced. ♦ Chemical dehalogenation reaction Decrease * area> Note I Relative biological decomposition reaction is gradually becoming an advantage > However, dechlorination is a long-term intuition j. It is going on. When the biological dehalogenation reaction starts to work, the halogenation has a coking term. Fill 1 The concentration of chemical pollution has been considerably reduced. 1 It will not become a biological dehalogenation reaction. V 1 Concentration barriers r will become the most low-level pollution that can be exerted by biological reactions. 1 Desulfurization, _ >-· 1 I halogenation reaction More active 0 Therefore * In the purification effect of halogenated I 1 1 compound pollution due to halogenation »From chemical dehalogenation reaction and biological dehydration 1 1 Order 1 The interaction of the dentification reaction can be purified to a very low level Concentration 〇 The chemical and biological radon degassing method of the present invention »Combining low-solubility 1 1 soil modifiers with inorganic% substances and organic matter, not only does 1 1 cause halogenated organic compounds to be dissolved in the polluted soil radon »And because the water retention of the contaminated soil is maintained, the halogenated organic compound is not polluted and re-infiltrated 1 I into the deep ground below the contaminated site M * Therefore > It can be cheap in a short period of time and J 1 I simply purifies the halogenated organic compound to contaminate the soil. 0 1 1 The reaction of the present invention * can be carried out until W. The monthly dechlorination reaction is completed * 1 1 This is the best case for the full purification of halogenated organic 1 1 compound pollutants, such as the purification of tetrachloroethylene and 2 1 1 gas ethylene pollutants. * The main product is TC ethylene free of chlorine > 1 j Acetyl organic compound 1 In this reaction, there is almost no harmful intermediate product containing atmosphere 1 I Product 1 can obtain excellent results. 0 1 1 This paper uses the Chinese National Standard (CNS) Λ4 specification (210X297). 23 39498 438621 A7 B7 V. Description of the invention (24) In the second aspect of the present invention, the kangen agent used in the first aspect of the present invention can be used. The halogenated compounds can be decomposed even when no specific host source is added and there is no biological reaction. The rhenium agent used in the third aspect and the fourth aspect of the present invention will be described below. In the third aspect and the fourth aspect of the present invention, a suitable activator having a standard electrode potential of the pseudo-hydrogen electrode at 25t of 130nV to -2400mV can be used. Preferably, the reducing agent used in the first aspect or the second aspect of the present invention is used. However, the rhenium agent used in the third aspect and the fourth aspect of the present invention is not limited to the original agent used in the first * 1 aspect and the second aspect of the present invention, and can be used as: Tangled iron, raw), manganese, nickel, magnesium, copper. The metal susceptible to gold, manganese and manganese exist in a large amount in an oxidized state in natural soil, and even if the addition has a small impact on the ecosystem, it is safe. In addition, it is easily accessible because it is trafficked. The amount of the primordial solution used is as described above. The kangen agent used in the third aspect and the fourth aspect of the present invention has a standard electrode position of -400bV to -2400bV at 25 υ for a standard hydrogen electrode. Gold tincture is preferred. It is preferable that at least one selected from the group consisting of the above-mentioned virgin agent M, suitable raw material I, raw material, silicon-alloy, titanium alloy, zinc alloy, manganese alloy, aluminum alloy, magnesium alloy, and calcium alloy. In addition, the aforementioned transport agent is preferably a water-soluble compound. The aforementioned transport agent is also preferably a powder having a particle size of 500w βK. The third aspect of the present invention will be mainly described below. The common features with the first aspect of the present invention will be omitted. In the third aspect of the present invention, it includes a transport agent that sets the 25C counter-quasi-hydrogen electrode to a quasi-electrode position of 130 nV-2400 iaV and a slave-type anaerobic withdrawal. (This page)

V 訂 本紙張尺度適用中國國家標準(CNS ) Α4規格(210X 297公釐) 24 39498 438621 A7 B7 經"部中央栲準局員了消費合作社印繁 五、發明説曰/ ( 25 ) 生 物 之 營 養 源 添 加 於 朋 述 污 染 物 中 之 步 驟 t 由 此 而 可 如 上 述 地 經 由 m 原 性 脫 鹵 化 分 解 鹵 化 有 機 化 合 物 〇 本 發 明 之 第 3 態 樣 中 » 前 述 營 養 涯 以 有 機 態 碳 及 含 前 述 有 機 態 碳 之 20 50 重 量 % 氧 化 態 氮 及 含 刖 述 有 機 態 碳 之 20 30 重 量 % 氧 化 m 氮 為 佳 〇 此 可 使 分 解 鹵 化 有 櫬 化 合 物 時 的 墦 原 性 脫 鹵 化 反 應 相 關 微 生 物 群 發 生 變 化 > 抑 制 磙 化 嫌 等 使 土 壊 變 黑 及 產 生 硫 酵 等 惡 臭 氣 體 0 此 處 氧 化 態 氮 之 含 量 9 例 如 硝 酸 塩 之 埸 合 指 硝 酸 塩 中 所 含 氮 原 子 之 重 量 〇 同 樣 地 9 有 機 態 碳 之 含 量 指 有 m 物 中 所 含 碳 原 子 之 重 量 0 - 埋 原 性 脫 鹵 化 中 1 由 添 加 營 着 源 之 成 份 土 壤 中 會 發 生 硫 酸 缠 原 > 甲 垸 醱 酵 等 生 物 性 遒 原 反 應 • 因 此 可 能 產 生 硫 化 氫 磙 酵 等 惡 臭 氣 體 及 甲 烷 氣 Αγν 夺 可 燃 性 氣 體 0 此 外 • 缠 原 條 件 下 金 層 粉 末 與 水 反 應 則 產 生 氫 氣 〇 另 外 > 亦 有 m 酸 m 原 而 結 果 產 生 硫 化 嫌 使 土 壤 變 黑 的 場 合 〇 但 營 養 源 中 含 有 櫬 態 碳 之 20 50 重 量 % 之 氧 化 態 氮 的 場 合 1 可 抑 制 此 等 反 應 〇 亦 即 , 利 用 土 壤 試 驗 已 確 定 生 長 基 質 之 有 機 態 碳 源 主 要 為 氧 化 態 氮 堪 原 活 性 微 生 物 所 利 用 9 因 此 而 抑 制 甲 院 醱 酵 及 硫 酸 埋 原 反 應 〇 土 壤 中 主 要 產 生 氮 氣 * 而 氮 氣 可 以 稀 釋 產 生 的 氫 氣 9 因 此 無 發 火 爆 發 之 顧 慮 0 此 外 > 因 曾 着 源 中 添 加 的 物 質 不 使 用 含 硫 成 份 或 硫 酸 根 之 塩 類 » 更 可 確 實 抑 制 硫 化 氫 碕 酵 系 氣 體 及 硫 化 m 產 生 0 污 染 物 中 添 加 過 ft 氧 化 態 氮 塩 之 場 合 9 因 為 有 機 態 氮 本紙張尺度適用中國國家標準(CNS ) A4規格(210X297公釐) 25 39498 # 先 閲 背 1¾ 之 注 意 事 項 再 填 寫 本 頁 438621 A7 B7 蚵潢部中决#卑局負工消费合竹社印來 五、發明説明( 26 ) 1 1 消 耗 後 會 遣 留 氧 化 態 氮 9 因 此 無 法 維 持 充 份 的 适 原 環 境 。例 1 | 如 僅 能 降 低 對 飽 和 氯 化 銀 電 極 之 氧 化 m 原 電 位 至 + 100 mV程 1 I 度 時 需 要 注 意 會 變 成 幾 乎 無 法 進 行 遢 原 性 脫 鹵 化 反 應 0 請 1 1 先 1 此 外 » 相 反 地 在 氧 化 態 氮 源 添 加 量 相 對 於 有 機 態 碳 源 極 端 閱 讀 背 1 不 足 的 場 合 初 期 時 產 生 之 氮 氣 幾 乎 耗 盡 氧 化 態 氮 因 此 面 I 之 1 注 | 其 後 將 發 生 甲 烷 醱 酵 等 般 的 生 物 性 缠 原 反 懕 〇 因 此 • 添 意 事 項 •丨‘ 1 加 的 有 櫬 態 碳 源 與 氧 化 態 氮 源 之 比 例 即 甚 為 重 要 0 再 填 1 Λ - 般 已 知 P 具 遢 原 氧 化 m 氮 活 性 微 生 物 之 A 1 c a 1 i κ e n e S 寫 本 L e u t η Q Ρ h u a r a c 〇 〇 c U d ft n i t Γ i f 1 〇 a j\ _Sl^水溶液中氣化 頁 1 1 態 氮 之 消 耗 率 為 有 機 碳 源 之 40 50重 量 % 但 發 明 人 等 以 ! 1 I 各 種 土 壤 中 原 生 菌 進 行 本 發 明 之 缠 原 反 應 的 结 果 添 加 的 1 訂 氧 化 態 氮 為 有 機 態 碳 源 之 20 50重 董 % 9 或 者 更 好 是 20 1 30重 量 % 比 例 添 加 之 場 合 » 均 無 甲 院 f 硫 黃 系 惡 臭 氣 體 產 1 1 生 » 且 氧 化 m 氮 塩 完 全 消 失 而 鹵 化 有 機 化 合 物 可 達 成 完 全 1 1 之 脫 鹵 化 〇 厂'' 已 往 認 為 在 堪 原 性 脫 鹵 化 反 應 進 行 中 添 加 氧 化 態 氮 將 } \ I 妨 礙 反 應 進 行 (艤田等, P Γ 0 C . 8 t h I n t e r n a t I ο η a 1 C on t * 1 1 I on a n a e r 〇 b i C D i g e s t 1 on » 1 9 97 年 t 第 2 卷 » 49 2, -4 9 9 頁 1 ί )〇 但本發明中適當調節氧化態氮與有櫬態碳之添加比例, 1 1 可 Μ 防 止 具 氧 化 態 氮 還 原 活 性 之 微 生 物 占 優 勢 而 產 生 硫 磺 1 1 系 惡 臭 氣 體 及 甲 院 等 可 燃 性 氣 艚 i 且 維 持 污 染 物 中 的 堪 原 1 1 狀 態 * 使 僅 由 金 屬 粉 末 無 法 達 成 的 安 定 有 效 之 脫 鹵 化 反 1 I 應 成 為 可 能 〇 因 此 本 發 明 可 謂 為 打 破 已 注 常 識 之 新 淨 化 方 1 I 法 0 1 1 本紙賴用中國國酬cnS ) Μ規格(训x騰麓) 3 9 4 9 8 438621 B7 經"部中决精準局員工消费合作社印" 五、發明説明( 27 ) 1 I 氧 化 態 氮 Μ 硝 酸 塩 形 態 為 佳 0 前 述 硝 酸 塩 含 有 m 金 1 | 屬 m 酸 塩 Λ m 土 金 屬 硝 酸 塩 > 硝 酸 鐵 Λ 硝 酸 钛 > 硝 酸 鋅 、 1 I 硝 酸 錳 、 硝 酸 鋁 及 硝 酸 鎂 者 為 佳 * 前 述 硝 酸 塩 >Λ 含 有 硝 酸 1 1 納 硝 酸 鉀 或 硝 酸 鈣 者 為 更 佳 〇 先 閱 讀 1 1 本 發 明 中 有 檐 態 碳 之 供 給 水 溶 性 有 機 碳 涯 為 佳 0 然 背 之 I 而 不 限 於 本 發 明 之 第 3 m 樣 者 t 使 用 本 發 明 之 第 1 態 漾 注 意 事 1 •丨· 及 第 4 態 樣 亦 可 0 水 溶 性 有 機 態 碳 以 糖 類 有 機 酸 及 其 衍 項 再 填 寫 本 頁 1 Λ | 生 物 低 級 酵 、 m 糖 蜜 液 或 者 醱 酵 廢 液 及 其 混 合 物 為 佳 〇 有 機 態 碳 有 生 長 基 質 之 作 用 j 使 m 生 物 可 Μ 生 長 0 有 櫬 1 I m 碳 亦 可 利 用 匍 萄 糖 N m 糖 等 糖 類 Ν 醋 酸 榫 棰 酸 乳 1 1 j 酸 等 有 機 m 或 有 欐 m 塩 1 耱 蜜 廢 液 醱 酵 m 液 啤 酒 酒 粕 1 % 豆 渣 等 有 機 性 廢 液 廢 棄 物 〇 有 機 態 碳 之 添 加 量 須 先 考 訂 ί 慮 污 染 物 所 具 有 的 氧 化 力 及 鹵 化 有 機 化 物 之 污 染 濃 度 後 1 1 再 決 定 > 但 污 染 物 為 一 般 不 胞 和 土 壤 之 埸 合 » 為 維 持 m 原 1 1 狀 態 t 對 1 k g之土壤必須添加約1 kg 的 有 機 態 碳 0 此 外 ,脫 鹵 化 對 象 之 鹵 化 有 機 化 合 物 之 污染濃度超過5〇Bg/ kg 之 場 τ I 合 > 對 l*g之鹵化有機化合物之添加量必須增加1 0 〜2 0 a g 1 1 | 比 例 的 有 機 態 碳 〇 但 此 均 為 種 標 準 ♦ 實 際 的 污 染 現 場 中 1 1 不 僅 有 污 染 物 之 氧 化 力 而 已 * 雨 水 或 空 氣 供 給 的 氧 氣 亦 會 1 1 消 耗 有 機 態 碳 及 後 述 金 靥 粉 末 之 堪 原 力 9 因 此 須 在 現 場 進 1 1 行 Ί_·,· 月U 置 試 驗 後 再 決 定 各 個 添 加 濃 度 〇 1 1 本 發 明 第 4 態 樣 為 含 鹵 化 有 機 化 合 物 % 固 髑 之 污 染 物 1 I 的 淨 化 方 法 0 污 染 物 如 上 述 ♦ 本 發 明 之 第 4 態 樣 包 含 在 污 1 1 I 染 物 中 棍 合 特 定 營 着 液 及 特 定 m 原 劑 之 步 驟 0 此 混 合 步 驟 1 1 本紙張尺度適用中國國辦(™規格⑽x騰楚) 3949 8 438621 B7 經"—部中次標準局員^-消費合作社印製 五、發明説明( 28 ) ! | 並 調 節 污 染 物 於 PH4 . 5〜9 .0之範 _ 〇 I 1 Μ、丨於_ 月ϋ 述 适 原 劑 為 粉 末 形 態 時 » 最 好 將 » -r- 刖 述 營 養 物 添 加 於 1 1 1 月[) 述 污 染 物 中 f 再 混 合 之 , 其 次 將 m 述 m 原 劑 添 加 人 前 述 請 1 1 1 混 合 物 中 1 再 次 再 混 合 之 0 如 此 可 防 止 适 原 劑 在 曾 養 先 閱 讀 背 ιέ 之 1 1 液 中 氧 化 , 使 进 原 力 可 在 污 染 物 中 發 揮 〇 1 或 者 9 » *·. 刖 述 還 原 劑 為 水 溶 性 化 合 物 而 前 述 堪 原 劑 溶 注 意 事 丨 | 解 於 月U 述 營 養 液 中 亦 佳 〇 如 此 在 現 場 較 固 級 通 原 劑 更 容 易 項 再 填 1 實 施 〇 同 時 大 量 營 着 液 之 保 存 移 動 亦 容 易 0 此 外 , 為 防 寫 本 頁 I 止 理 原 m 在 保 存 中 氧 化 9 含 m 原 劑 之 營 養 液 最 好 保 存 在 密 ·- 1 1 閉 容 器 内 0 1 ! | 在 混 合 步 驟 中 t 營 着 液 亦 可 以 分 2 次 >λ 上 添 加 在 污 染 1 訂 丨’ 物 中 〇 大 量 的 營 着 液 在 例 如 與 土 壤 棍 合 之 場 合 » 因 為 液 體 中 土 壤 塊 之 切 m 力 難 K 作 用 1 因 此 土 壤 塊 無 法 崩 裂 > 在 液 1 1 體 中 不 易 移 動 〇 相 對 於 此 * 添 加 之 營 養 液 少 量 的 場 合 * 可 1 i Η 更 易 由 切 斷 力 使 土 塊 崩 裂 * 易 於 混 合 得 更 均 勻 〇 因 此 可 以 再 在 其 次 時 添 加 更 多 的 曾 養 液 0 簧 施 樣 態 之 一 i 即 最 r I 好 在 第 1 階 段 之 步 嫌 中 t 在 ^ > 刖 述 污 染 物 中 添 加 混 合 前 述 污 1 1 染 物 量 之 1〜10體積%的前述營養液, 其次再Μ步驟在前 1 1 述 污 染 物 中 添 加 \ 混 合 較 第 1 階 段 之 添 加 量 更 大 量 的 前 述 1 1 營 養 液 0 其 他 之 實 雎 樣 態 最 好 是 第 1 階 段 之 步 驟 在 前 逑 1 ί 污 染 物 中 添 加 混 合 .If. 刖 述 污 染 物 量 之 1〜5 體積%的前述 1 1 營 養 液 » 其 次 之 第 2 階 段 步 驟 再 於 W· 刖 述 污 染 物 中 添 加 > 混 1 I 合 與 第 1 階 段 合 計 為 刖 述 污 染 物 量 之 5〜10體積%的前述 1 1 I 營 養 液 9 另 外 再 由 步 驟 在 t > 刖 述 污 染 物 中 添 加 > 混 合 比 第 1 1 1 本纸張尺度適用_家標準(⑽Μ規格(膽腾董) 3 9498 kl 經濟部中央標準局員工消費合作社印製 438621 ____ B7 五、發明説明(2 9 ) 階段及第2階段中添加量更大量的前述營養液。但無論實 施樣態如何s在第1階段中僅添加少童之營養液,因此混 合物中切斷力易發揮,可更容易地混合。在任一實施樣態 中,前述污染物中添加之前述營養液以最終為前逑污染物 量之15〜25體積%為佳。所謂之最终,即指在曾養液分數 次添加的場合營養液之總和。 其次,將混合物在低通氣條件下靜置。靜置工程中堪 原性脫鹵化即可除去污染物。例如靜置2遇以上,靜置 1個月Μ上則更隹。 靜置步驟Μ與周園隔鐮的之狀態為佳。如此可以防止 混合物中鹵化有櫬化合物擴散、滲透至周圍。 為維持低通氣條件,前述汚染物最好覆蓋不通氣材料 。例如覆蓋聚氣乙烯塑膠布為佳。此乃是為促進厭氣性撤 生物之培養。為維持低通氣條件,前述污染物最好浸於水 溶液中。 前述靜置步驟中,前述污染物最好在至少最初的3曰 保持在17〜60TC,如此可Μ促進混合物中微生物之培養以 提高濃度。前述靜置步驟中,前述污染物Μ至少在最初的 5日保持在17〜60C為佳。前述靜置步驟中,前述污染物 能在至少最初的3日,最好是5日,保持於20〜40¾則更 佳。 奮撫例 Μ下K實施例具體說明本發明。但本發明並不限於此 些實施例。 本紙張尺度適用中國國家標準(CNS ) Α4規格(210X297公釐) (請先閲讀背面之注意事項再填寫本頁}The paper size of the V edition applies to the Chinese National Standard (CNS) A4 specification (210X 297 mm) 24 39498 438621 A7 B7 The member of the Central Bureau of Standards of the Ministry of Economic Affairs of the People's Republic of China printed the fifth, the invention said / (25) Biological nutrition The step t of adding the source to the pollutant can thus decompose the halogenated organic compound via m-original dehalogenation as described above. In the third aspect of the present invention »The aforementioned nutritional domain is composed of organic carbon and the aforementioned organic state. 20 50% by weight of oxidized nitrogen and 20 30% by weight of oxidized nitrogen containing the stated organic carbon are preferred. This can change the microbiome associated with the degenerative dehalogenation reaction when decomposing halogenated europium compounds > Suppression of susceptibility to blackening soil odor, and generation of malodorous gases such as sulfur fermentation. Here the content of oxidized nitrogen is 9. For example, the combination of osmium nitrate refers to the weight of nitrogen atoms in osmium nitrate. Similarly, 9 organic state The content refers to the weight of the carbon atoms contained in the m. 0-In the process of dehalogenation. 1 By adding the source ingredient, the soil will cause entrapment of sulfuric acid > Malodorous gases such as hydrogen sulfide fermentation and methane gas Αγν may be generated. In addition, • The gold layer powder reacts with water to generate hydrogen under entrapped conditions. In addition, there are also m acids and m sources, and as a result, sulfur is suspected to cause soil pollution. Where it turns black, but where the nutrient source contains 20 to 50% by weight of oxidized nitrogen in the form of carbon, 1 these reactions can be suppressed. That is, the organic carbon source of the growth substrate has been determined to be mainly in the oxidized state by soil tests. Nitrogen can be used by active microorganisms9 As a result, the inhibition of Ayuan fermentation and sulphuric acid burial reaction is inhibited. 0 Nitrogen is mainly produced in the soil. Generated hydrogen 9 so there is no concern about pyrophoric explosions 0 In addition > Because the materials added to the source do not use sulfur-containing components or sulfate radicals »It can more reliably inhibit hydrogen sulfide fermentation gas and sulfide m from generating 0 pollutants Where ft is added in the oxidation state of nitrogen 9 9 Because the organic nitrogen is sized in accordance with the Chinese National Standard (CNS) A4 (210X297 mm) 25 39498 # Please read the precautions on the back 1¾ before filling out this page 438621 A7 B7 蚵部 部 中 定 #Beijuan, overworked and consumed by the Hezhu Society 5. Introduction to the Invention (26) 1 1 Oxidized nitrogen will be retained after consumption 9, so it is impossible to maintain a sufficient suitable environment. Example 1 | If you can only reduce the oxidized m potential of the saturated silver chloride electrode to + 100 mV range 1 I degree, you need to pay attention that it will become almost impossible to perform the degenerative dehalogenation reaction. 0 Please 1 1 first 1 In addition »Conversely When the amount of oxidation-state nitrogen source added is extreme compared to the organic-state carbon source, the amount of nitrogen generated at the beginning is almost depleted of the oxidation-state nitrogen. Therefore, surface I-1 Note |原 原 反 懕 〇 Therefore • Adding notes • 丨 '1 The ratio of the carbon source with carbon dioxide and the nitrogen source with oxidation state is very important. 0 then fill in 1 Λ-Generally known. A 1 ca 1 i κ ene S manuscript Leut η Q Ρ huarac 〇〇c U d ft nit Γ if 1 〇aj \ _Sl ^ Gasification in aqueous solution 1 1 The consumption rate of nitrogen is organic carbon source 40 50% by weight, but the inventors have added! 1 I added as a result of the protozoan reaction of various soils in the present invention 1 order of oxidation state nitrogen as the organic carbon source 20 50% by weight 9 or better 20 1 When 30% by weight is added in proportions »No Jiayuan f sulphur yellow malodorous gas produced 1 1» and the oxidation of nitrogen and nitrogen has completely disappeared and halogenated organic compounds can reach a complete 1 1 dehalogenation plant. The addition of oxidation state nitrogen during the degenerative dehalogenation reaction will} \ I hinder the reaction (Putian et al., P Γ 0 C. 8 th I nternat I ο η a 1 C on t * 1 1 I on anaer 〇bi CD igest 1 on »1 97 1997 t Vol 2» 49 2, -4 9 9 Page 1 ί) 〇 However, in the present invention, the addition ratio of oxidized nitrogen and fluorinated carbon is appropriately adjusted, 1 1 can prevent oxidation Nitrogen reducing active microorganisms predominate and produce sulfur 1 1 series malodorous gas A flammable gas, such as a hospital, maintains the original 1 1 state in the pollutant *. It should be possible to achieve a stable and effective dehalogenation reaction 1 I that cannot be achieved by metal powder alone. Therefore, the present invention can be said to break the common sense. New Purification Method 1 I Method 0 1 1 This paper relies on China's national compensation cnS) M specifications (Training x Tenglu) 3 9 4 9 8 438621 B7 Economics & Printed by the Ministry of China Precision Industry Bureau Consumer Consumption Cooperatives V. Description of the invention (27) 1 I oxidation state M 塩 塩 nitrate form is better 0 The aforementioned 塩 塩 contains m gold 1 | belongs to m 塩 塩 m earth metal 塩 > iron nitrate Λ titanium nitrate > zinc nitrate, 1 I manganese nitrate, aluminum nitrate and Magnesium nitrate is better * The aforementioned hafnium nitrate > Λ contains nitric acid 1 1 potassium nitrate or calcium nitrate is better. Read first 1 1 In the present invention, it is better to supply water-soluble organic carbon. I without In the 3m sample of the present invention t Use the first aspect of the present invention 1 • 丨 and the 4th aspect can also be 0 Water-soluble organic carbon with sugar organic acids and their derivatives Please complete this page 1 Λ | Bio-lower fermentation, m molasses solution, or fermentation waste solution and mixtures thereof are preferred. Organic carbon has the function of a growth matrix. J Makes m organisms grow 0. There is 1 I m. Carbon can also use glucose N m Sugars and other sugars N Acetic acid vinegar yogurt 1 1 j Organic acids such as acid or 欐 m 塩 1 耱 Honey waste liquid fermentation Fermented liquid beer lees 1% Organic waste liquid waste such as bean dregs o The amount of organic carbon added must be First consider the oxidizing power of the pollutants and the concentration of the halogenated organic compounds 1 1 before deciding > But the pollutants are generally a mixture of soil and soil »To maintain the original state of m 1 1 t to 1 kg The soil must be added with about 1 kg of organic carbon. The concentration of the halogenated organic compound whose halogenated object is more than 50Bg / kg in the field τ I combined> The amount of halogenated organic compound added to 1 * g must be increased by 1 0 ~ 2 0 ag 1 1 | ratio of organic carbon. However, this is a standard. ♦ In actual pollution sites, 1 1 not only has the oxidizing power of pollutants, but also the oxygen supplied by rain or air. 1 1 Consumption of organic carbon and the rigorous power of gold powder described below. 9 Perform 1 1 on-site to determine the concentration of each additive after the test is performed. 0 1 1 The fourth aspect of the present invention is a halogenated organic compound% solid pollutant 1 I purification method 0 The pollutant is as above ♦ The fourth aspect of the present invention includes a step of sticking a specific carrier liquid and a specific m original agent in the stain 1 1 I dye. This mixing step 1 1 This paper size is applicable to the State Council of China (™ size⑽x 腾 楚) 3949 8 438621 B7 Economic " —Middle and Medium Standard Bureau Member ^- Printed by Fei Cooperative Co., Ltd. 5. Description of the invention (28)! | And adjust the pollutants to a range of PH 4. 5 ~ 9 .0 _ 〇I 1 Μ, 丨 _ Yue ϋ When the appropriate agent is in the form of powder »it is best to »-R- Add the nutrient in 1 [January] [] and remix the f in the pollutant, and then add the m or m original agent to the above please 1 1 1 1 in the mixture and then re-mix 0 to prevent The oxidizing agent is oxidized in the 1 1 liquid that was previously read, so that the priming force can be exerted in the pollutants 0 or 9 »* .. The reducing agent is a water-soluble compound, and the aforementioned priming agent is soluble. Note It ’s better to understand in the nutrient solution described in the month. So it ’s easier to fill in the field than the solid-level protozoal agent. Reimplement it at the same time. At the same time, it is easy to save and move a lot of liquids. In addition, to prevent writing this page I Zhiliyuan m is oxidized during storage 9 The nutrient solution containing m source is best stored In a tightly closed container-1 1 0 1 | | In the mixing step, the solution can be added to the contamination 1 in 2 times. A large amount of solution is mixed with the soil stick, for example. Suitable occasions »Because the soil mass in the liquid is difficult to cut m, the force K is difficult to act 1 so the soil mass cannot be broken > It is not easy to move in the fluid 1 1 body. Relative to this * When a small amount of nutrient solution is added * can be 1 i Η easier The soil is broken by the cutting force. * It is easy to mix more evenly. Therefore, it can be added at the next time. Once more nutrient solution is added. 0 One of the spring application states, i.e., the best r I is in the first stage. ^ > Add 1 ~ 10% by volume of the aforementioned nutrient solution to the above-mentioned pollutants and add the above-mentioned pollutants to the pollutants, and then add M to the above-mentioned pollutants in the first 11 steps. \ The mixing is more than that in the first stage. A lot of the aforementioned 1 1 nutrient solution 0 other fruits It is best to add and mix the first step in the first stage of the contamination. If. The above mentioned 1 1 nutrient solution is 1 to 5 vol% of the amount of the contaminated »The second stage step is followed by W · Add to the above-mentioned pollutants> Mix 1 I and the first stage add up to 5 to 10% by volume of the above-mentioned pollutants 1 1 I nutrient solution 9 In addition, add t to the above-mentioned pollutants in steps > Mixing ratio No. 1 1 1 This paper size is applicable _ home standard (⑽Μ specifications (Dan Tengdong) 3 9498 kl Printed by the Consumers' Cooperative of the Central Standards Bureau of the Ministry of Economy 438621 __ B7 V. Description of the invention (2 9) stage and In the second stage, a larger amount of the aforementioned nutrient solution is added. However, regardless of the implementation state, only the nutrient solution for young children is added in the first stage. Therefore, the cutting force in the mixture is easily exerted, and the mixture can be mixed more easily. In any embodiment, the nutrient solution added to the pollutant is preferably 15 to 25% by volume of the amount of the former pollutant. The so-called final refers to the sum of the nutrient solution in the occasion where the nutrient solution has been added several times. Second, the mixture was left to stand under low aeration conditions. Contaminant dehalogenation in a standing project removes contaminants. For example, it is more difficult to stand for 2 or more, and it is more to be left for 1 month. The standing state M is preferably separated from Zhou Yuan's sickle. In this way, halogenated hafnium compounds in the mixture can be prevented from diffusing and penetrating to the surroundings. In order to maintain low aeration conditions, the aforementioned pollutants are preferably covered with non-aerated material. For example, it is better to cover with polyethylene plastic cloth. This is to promote the cultivation of anaerobic organisms. To maintain low aeration conditions, the aforementioned contaminants are preferably immersed in an aqueous solution. In the aforementioned standing step, the aforementioned pollutant is preferably maintained at 17 to 60 TC for at least the first 3 days, so as to promote the cultivation of microorganisms in the mixture to increase the concentration. In the aforementioned standing step, it is preferable that the aforementioned pollutant M is maintained at 17 to 60C for at least the first 5 days. In the aforementioned standing step, the aforementioned pollutants can be maintained for at least the first 3 days, preferably 5 days, and more preferably between 20 and 40¾. Exemplary Examples The following examples specifically illustrate the present invention. However, the present invention is not limited to these embodiments. This paper size applies to Chinese National Standard (CNS) Α4 specification (210X297 mm) (Please read the precautions on the back before filling this page}

3 9498 29 4 3 86 2 1 Λ7 B7 五、發明説明(3〇 ) 本發明之賁施例中四氛乙烯之淨化實驗,撖生物培養 基係使用表1之申烷生成微生物用培着基,或表2之碳醸 适原微生物用培養基。各淨化實驗均在室灌(12〜23C )下 實施。 PH之澜定係諝節土壤:純水=1: 1(重量比),再Μ東 亞罨波工業製造的pH計HM-5b型测定。對飽和氯化銀電極 之氧化遢原轚位之測定,則諝節土壤:無氧水=1: 1(重 量比),再將東亞電波工業製造之ORP計0D1C-3型之ORP複 合電極PS-8160型浸人,放置30分鐘後澜定。 土壤中氯化乙烯類之分析,則依日本横濱國立大學開 發之方法(宮本建一等,「土壤之低沸點有檐污染物質含 量之測定方法」,水環境學會誌,1 995年,第18卷,第6 號,第47?〜488頁 >,將土壤試驗樣品浸於乙酵中由乙酵 萃取乙烯類後,再以癸烷萃取乙烯類,再將乙烯類之癸综 溶液注入日立氣相層析儀G-5000型之管柱内,WFID檢拥 器分析β 氣相中產生的氣化乙烯類氣體之測定,係將產生的氣 經濟部中央標準局員工消費合作社印製 (請先閱讀背面之注意事項再填寫本頁) 化乙烯類氣顥注人日立氣相層析儀G-5000型之20%TCP chΓoιlosorbWAWDHCS60〜80Besh管柱,MFID檢测器 檢测分析。測定氣相中產生的乙烯、乙烷氣體之場合,使 用Porapack Q管柱,日立氣相曆析儀G-5000型、FID檢拥 器檢测分析。氣相中產生之氫、二氧化碳氣、甲烷之痴定 ,以GL-科學氣相層析儀- 320型,TCD檢測器、活性碳30/ 60或 Mclecular Sieve 13X分析。 本紙張尺度適用中國國家標準(CNS ) Λ4^格(210X297公釐) 30 39498 438621 Λ7 經濟部中央標準局員工消費合作社印製 B7五、發明説明(3 1 ) 還原锇使用和光純槩工業股份有限公司、和光1鈒理 原锇,商品編號0 9 6 - 0 0 7 8 5。除非特別明載i邐原樺指粉 末。 實施例1〜5,及7〜10主要與本發明之第1態樣有Μ 〇 g倫俐1 實施例1中通原爾使用還原鐵粉末。 使用A工廠之污染土壤表層採取的污染土壤。該污染 土壤中之污染物質主要為四氯乙烯,Iks乾堍污染土壤中 所含之四氯乙烯量為25mg。M125ml容量之樣品瓶各採取 30g之此污染土壤14個,Μ K下所示14種實驗條件,測定 污染土壤之pH、對飽和氛化銀電極之氧化通原電位及四氯 乙烯減少量之各時間變化。各實驗組實施之含水率為48〜 50%範圍。樣品調整及樣品採取後均充以氮氣取代樣品瓶 之氣相部份。 試驗污染土壤採取自塲土層,其物理特性為含水率 47%,透水係數10_4〜10~5cm/sec, PH6.6,對飽和氯化 銀電槿之氧化堪原電位為380mV。 實驗條件: A.使用甲烷生成微生物用培着基(表1)反應姐 (請先閲讀背面之注意事項再填寫本頁} 基 養 培 成 生 組烷 制甲 控 + 壤壤 土土 染染 污污 ①② 壤埔 土土 染染 污污 ③Φ 基 養 培 成 生 烷 甲 基 着 培 成 生 烷 甲 0 0 原 原 堪缠 混 本紙張尺度適用中國國家標準(CNS ) A4規格(210 X 2?7公釐) 31 3 9 49 8 A7 經潢部中"標準局员工消贽合作社印製 438621 __ B7 五、發明説明(32 ) 合石灰霣肥料A (主成份石灰石)l.〇s +牛糞堆肥1.0s +腐葉土 0 . 5 g3 9498 29 4 3 86 2 1 Λ7 B7 V. Description of the invention (30) The purification experiment of the four atmosphere ethylene in the example of the present invention, the biological medium is the culture medium used in Table 1 to produce microorganisms, or Table 2 is a medium for carbohydrate-producing microorganisms. Each purification experiment was performed under a chamber irrigation (12 ~ 23C). The soil of the Phyllanthus pupae was determined by pure water = 1: 1 (weight ratio), and then measured by a pH meter HM-5b manufactured by Miyako Industrial Co., Ltd. For the measurement of the original tritium oxide position of the saturated silver chloride electrode, the soil: anaerobic water = 1: 1 (weight ratio), and the ORP meter 0D1C-3 type ORP composite electrode PS made by East Asia Radio Industry Type -8160 is immersed in humans. After 30 minutes of standing, it will be stable. The analysis of vinyl chloride in soil is based on the method developed by Yokohama National University in Japan (Miyamoto Kenichi et al., "Measurement Method for Pollution Content of Low-boiling Point Eaves in Soil", Journal of the Water Environment Society, 1995, 18th Volume 6, No. 6, pp. 47 ~~ 488 > After immersing the soil test sample in acetic acid to extract the ethylene from the acetic acid, then extract the ethylene with decane, and then inject the ethylene decyl complex solution into Hitachi In the column of the gas chromatograph G-5000, the WFID detector analyzes the gasification of ethylene gas produced in the β gas phase. It is printed by the Consumer Cooperative of the Central Standards Bureau of the Ministry of Gas Economy (please (Read the precautions on the back before filling this page.) Polyethylene gas injection into the Hitachi G-5000 20% TCP chΓololosorbWAWDHCS60 ~ 80Besh column, detection and analysis by MFID detector. Determination of gas phase For the generation of ethylene and ethane gas, use Porapack Q column, Hitachi gas phase analyzer G-5000, FID detector to detect and analyze. The hydrogen, carbon dioxide and methane produced in the gas phase are determined. With GL-Scientific Gas Chromatograph-Model 320, TCD Detector, activated carbon 30/60 or Mcclecular Sieve 13X analysis. This paper size applies Chinese National Standard (CNS) Λ4 ^ grid (210X297 mm) 30 39498 438621 Λ7 Printed by the Consumer Cooperative of the Central Standards Bureau of the Ministry of Economic Affairs Explanation (3 1) Reduction 锇 Use of Wako Pure Chemical Industries Co., Ltd., Wako 1 Raw Materials, Article No. 0 9 6-0 0 7 8 5. Unless specifically stated, 载 hara birch finger powder. Examples 1 ~ 5, and 7 ~ 10 are mainly the same as the first aspect of the present invention. Moglun Li 1 In Example 1, Tongyuaner used reduced iron powder. The contaminated soil taken from the contaminated soil surface of the A factory was used. The polluting substance is mainly tetrachloroethylene, and the amount of tetrachloroethylene contained in the Iks dry contaminated soil is 25mg. M125ml capacity sample bottles each take 14 g of this contaminated soil, and 14 kinds of experimental conditions shown in MG, Measure the pH of contaminated soil, the oxidative potential of the saturated atmospheric silver electrode and the time variation of the reduction of tetrachloroethylene. The moisture content of each experimental group is in the range of 48-50%. Replace with nitrogen The gas phase part of the bottle. The contaminated soil in the test was taken from the soil layer. Its physical characteristics are 47% moisture content, water permeability coefficient 10_4 ~ 10 ~ 5cm / sec, PH6.6. The original potential was 380 mV. Experimental conditions: A. Use methanogens to form microorganisms (Table 1) to react (please read the precautions on the back before filling this page). Soil staining and soiling ①② Soil staining and soiling of Liaopu soil ③ Φ Basic culture and growth of alkyl alkane methylation and growth of raw alkane 0 0 The original paper can be mixed and mixed. The paper size is applicable to China National Standard (CNS) A4 (210 X 2 to 7 mm) 31 3 9 49 8 A7 Printed by the Ministry of Economic Affairs " Standards Bureau Consumers' Co-operative Co., Ltd. 438621 __ B7 V. Description of the invention (32) Lime and fertilizer A (main component limestone) l.〇 s + cow manure compost 1.0s + rotten leaf soil 0.5 g

⑤ 污染土壤+甲烷生成培養基9.0b1+®原截1.0S +混 合石灰質肥料B1主成份石灰石與沃植敏)1.0g十下水 道污泥堆El.〇s +腐葉土 0.5S ⑥ 污染土壤+甲烷生成培養基9.0b1+堪原鐵l.〇s +混 合貝骰化石肥料(主成份貝殻化石)1.0g +下水道污泥 堆 IE 1.0g + 腐葉土 0.5g ⑦ 污染土壤+甲垸生成培養基9.0ml +堪原嫌1.0g +混 合石灰質肥料A 1.0g +腐絮土 l.Og 此處之「沃植敏」為腐植酸菱苦土胞料,其組成份為 腐植酸(50〜60%)、菱苦土(15%)、總氮(3%)、矽酸 (3% )。 (請先閲讀背面之注意事項再填寫本頁)⑤ Contaminated soil + methane generation medium 9.0b1 + ® original cut 1.0S + mixed limestone fertilizer B1 main components limestone and Wo Zhimin) 1.0g ten sewer sludge piles El.〇s + rotten soil 0.5S ⑥ Contaminated soil + methane generation medium 9.0 b1 + Kanhara iron 1.0s + mixed shellfish fossil fertilizer (main ingredient shell fossil) 1.0g + sewer sludge pile IE 1.0g + rotten leaf soil 0.5g ⑦ contaminated soil + formazan production medium 9.0ml + Kanahara 1.0g + Mixed calcareous fertilizer A 1.0g + humic soil l.Og Here, "Wo Zhimin" is humic acid rhodochloite, and its composition is humic acid (50 ~ 60%), rhodochloite (15%) ), Total nitrogen (3%), silicic acid (3%). (Please read the notes on the back before filling this page)

表1 甲烷生成撤生物用培着基 成 分 組 成 自來水 8 0 0 b 1 無機塩溶液1 50m 1 /1 無機塩溶液2 50*1/1 無機扈溶液 1 Οι 1 / 1 維生素溶液 1 0a 1 /1 NaHCOs 5 . 0g/ 1 酵素萃取物 1 . Og/ 1 聚蛋白陳 20 g/ 1 葡萄糖 25 g/ 1 擰檬酸納 25 g/ 1 甲酵 50n 1 /1 L-半胱胺酸塩酸塩溶液 5 . 0m 1 / 1 Na2S * 9H2〇溶液 5.0e I / 1 pH 6 · 9 〜7 . 2 本紙張尺廋適用中國國家標準(CNS ) A4規格(210X297公f ) 32 3 9 498 438621 A7 B7五、發明説明(33 ) 前述實驗條件中,表示前述反應系之式所表示的內容 條 驗 實 之 5 ) 2 ④ 1 如在 例 下 如. 明: 說: 與 壤 土 染 污 之 S ο 3 將 中 瓶 品 樣 之 量 容 將 表 所 Μ 加及 添蓋 再膠 , 橡 中基 物丁 , 合上 後混蓋 合此 , 混入後 Α 加土 料基葉 肥蕃腐 質培之 灰用5g 石物0. 合生及 混微肥 之成堆 og生糞 1 烷牛 、 甲 之 鐵的og 原示 1 定 澜 並 示 所 圖 1 第 如 品 樣 試 測 種 7 述 前 之 〇 備 封預 密法 紙同 箔 鋁 之 銀 化 氛 和 飽 對 及 值 Η Ρ 的 後 曰 7 ' 量 含 烯 乙 氣 四 的 後 曰 3 組 應 反 xlr 2 表 /tv 基 養 培 用 物 定 生 測微 C 的 原 位示适 電所酸 原下磙 遢以用 化 使 氧B. 示 所 圖 1X 第 如 隔 間 (請先閱讀背面之注意事項再填寫本頁) 組 制 控 壤 土 染 污 ① 基基基 着養養 培培培 原原原 缠遢遢 酸酸酸 硫磙确 + + + I 8 I 土土土 染染染 污污污 ②③④ 锇 原 适 锇 原 适 混 石 灰 石 份 成 主 A 4 g 料 5 κ ο 質土 灰絮 石腐 合 + IB 堆 Μ 牛 基 養 培 原 0 酸 硫+ 墉 土 染 污 ⑤ 嫌 原 堪+ 混 料1. S 把 質堆 灰泥 石污 合道 敏 植 沃 與 石 灰 石 份 成 主 土 腐 水 下 g泥:S g 道 .0水 下 鐵 0 ^ 遢.0 1 + ) -1石 ο化 ^ 0 貝 養 ί 培 成 原 S 主 酸料 硫肥 + 石 壤化 土般 染貝 污 合 © 土 « 腐+ 本紙張尺度適用中國國家標準(C-NS ) Λ4規格(210Χ 297公釐) 33 3 9 498 438621 A7 B7五、發明説明(34 ) ⑦ 污染土壤+硫酸堪原培養基9.0»1+适原朗ll.〇s +混 合貝殻化石肥料(主成份貝殻化石)l.〇g +下水道污泥 堆肥1.0g +腐葉土 0.5g ⑧ 污染土壤+碲酸堪原培養基9.0inl +遢原餓1.0g +混 合石灰質肥料A (主成份石灰石)1.0g+腐第土 l.〇s + 腐葉土 0 . 5g 表2 硫酸适原微生物用培養基 成 分 組 成 自來水 1 0 0 0 b 1 K2HPO4 0 + 5 g / 1 NH4C 1 1 . 0g/ 1 N a 2 S 0 4 1 . 0g/ 1 CaC12 · 2H2〇 0 . Is/ 1 M g S 0 4 ♦ 7 H 2 0 2 . 0g/ 1 酵母萃取液 1 . 0g/ 1 FeS〇4 · 7H2〇 0.2g / 1 微量維生素溶液 1 0m 1 / 1 乳酸納 25m 1 / 1 酯酸納 25n 1 /1 乙硫酵酸納 0 . 1 g/ 1 抗壤血酸 0 . 1 g/ 1 pH 6 . 6〜7 . 0 (請先間讀背面之注意事項再填寫本頁} 本紙張尺度適用中國國家標率(CNS ) A4規格(210X297公釐) 34 3 9498 438621 A7 __B7_五、發明説明(35) 寶施例1之試驗结果示於第1睡及第2鼷。實驗 四 之 ⑤ r ④- S 驗 賁 及⑤ 、④ 1 A 驗 實 中 B 驗 實 及 ⑦'⑥ 。 各 物 中 。生 園料微 於肥原 載系 a 記機酸 不無硫 而及及 略嫌基 省原養 此還培 因合用 , 混物 同中生 相壤微 致土成 大染生 形污烷 情.,甲 的知與 少可再 減圈 , 烯由肥 乙 堆 氯 種 環 性 中 之 近 附 7 Η Ρ 在 壤 土 持 保 地 定 安Μ 可 合 混 基 養 培 用 外 此 ο 解 分 速 快Μ 可 烯 乙 氯 四 中 壤 土 境 環 性 氣 厭 及 境 分 法 無 並 壤 土 染 污 合 混 鐵 原 适Μ 僅 示 顯 圖 2 第 及 _ 1 第 可 亦 料 肥 質 灰 石 合 混 代 取 灰 石 消 用 使 次 其 〇 ί 〇 男 烯效 乙的 氯樣 四同 解得 氣 用 使 則 姐 制 控 0 末 粉 嫌 原 蓮 用 〇 使I) I0 ( 原截 還酸 中硫 2 及 例 、 施I) 資(I 鐵 化 再 後 壤 土 染 污 烯 乙 氯 四 取 採 廠Η A 之 同 相 11 例 施 實 § 例 施 實 k } 1 同 每 〇 為驗 成試 其後 使壤 整土 調度 ,澹 烯髙 乙之 氯烯 四乙 加氣 添四 含 約 中 壤 土 嫌 乾 壤 土 染 污 將 (請先聞讀背面之注意事項再填寫本頁) 於 裝 分 經濟部中央標準局®c工消費合作社印製 定 測 各 下 量 少 減 之 烯 乙 件 條 驗 - 、 實位碳 種電化 CO 原氧 下堪二 K 化 、 於氧氫 再之 、 , 極 量 中電生 瓶銀產 品化烷 樣氯乙 之和 、 量鉋烯 容對乙 氣 四 烷 甲 驗 實 0 行 進 園 範 % 3 5 ί 8 4 率 水 含 在 均 姐 驗 實 各 〇 量 生 ul-t 遽 各滅 土群 葉物 腐生 及撤 肥之 堆本 泥原 B 中 道其 水將 下 . 及鐘 壤分 土60 染菌 污殺 - 汽 中蒸 ④懕 B-高 驗釜 實菌 及殺 ④ 經 用份 作部 之相 物氣 生內 撤瓶 中 品 系樣 應代 反取 解氣 分氮 烯M 乙並 氛時 四整 討調 檢品 Μ 漾 菌 本紙張尺度適用中國國家標準(CNS ) Α4規格(2i〇X297公釐) 35 3949 8 4 3 86 2 1 at * B7 五、發明説明(36 ) 實驗條件: A. 使用甲烷生成微生物培着基(表1)反應組 ① 污染土壤+甲烷生成培養基9,0(〇1+1原鐵1.0g +混 合石灰質肥料B (主成份為石灰石及沃植敏)1.0g +下 水道污泥l,Og +腐葉土 〇.5g ② 污染土壤+甲烷生成培養基9.0ml + FeC丨2 l.〇s +混 合石灰質肥料B (主成份石灰石及沃植敏)1.0g +下水 道污泥堆肥1. 〇S +腐葉土 〇.5s ③ 污染土堳+甲烷生成培養基9,0iil + FeS〇4 1.0g +混 合石灰質肥料B (主成份石灰石及沃植敏)1.0g +下水 道污泥堆肥1.0g+腐葉土 0.5s ④ 滅藉#的污染土壤+甲烷生成培養基9.0al +埋原锇 l.〇g +混合石灰質肥料B (主成份石灰石及沃植敏) l.〇s +滅菌過下水道污泥堆肥l.〇g +姨.菌通腐葉土 0 . 5 g B. 使用碲酸遢原微生物用培養基(表2)反應組 經濟部中央標準局員工消費合作社印製 (請先閱讀背面之注意事項再填寫本頁) ① 污染土壤+硫酸堪原培養基9.0ml +還原鐵1.0g +混 合石灰質肥料B (主成份石灰石及沃植敏)l.〇g +下水 道污泥堆肥1.0g+腐葉土 0.5g ② 污染土壤+硫酸进原培養基9.0ml + FeClz l,0g +混 合石灰質肥料B (主成份石灰石及沃植敏)1.0g +下水 道污泥堆肥1.0s +腐植土 〇.5g ③ 污染土壤+碲酸遢原培養基9.0ml+FeS〇4 l.〇s +混 合石灰質肥料B (主成份石灰石及沃植敏)1.0g +下水 本紙張尺度適用中國國家標率(CNS ) A4規格(210X297公釐) 36 3 9 49 8 438621 Λ7 經濟部中央標準局員工消費合作社印製 B7五、發明説明(37 ) 道污泥堆肥1.0g+腐植土 0.5g ④減菌過的污染土壤+硫酸里原培養基9.0IB1+遏原鐵 1 . ¢) g +混合石灰質SB料Β (主成份石灰石及沃植敏) l.〇g +滅菌過的下水道污泥堆肥1.0g +滅菌過的腐葉 土 0 · 5 g 實施例2之結果示於表3及表4。 由表3及表4可知,堪原鐵可分解四氣乙烯。相對地 ,F e C 1 2、F e S 0 4等亞鐵塩或P e C1 3之雄塩並無法分解。同 時可知,污染土壤中混合堪原嫌及無機糸肥料(pH調節劑) 、各種堆脃,及甲烷生成微生物用培養基或硫酸堪原撤生 物用培養基,可Μ使土壤保持在PH7附近安定的中性環境 以及厭氣環境,使土壤中四氛乙烯可以快速分解。另外亦 知,添加FeCU或FeS〇4取代遢原嫌之場合,四氯乙烯之分 解幾乎無法進行。 此外,在微生物滅菌之場合(實驗A -④、B -④)中僅有 相當少的四氛乙烯分解量,顯示本發明之方法係由生物性 反應及化學性反應之相乘作用進行還原性脫鹵化反應 表4所示為實驗A-①、B-①中樣品瓶內產生氣體成份 之分析结果。可知在此些實驗組中均可生成大量的氫氣、 二氧化碳及乙烯、乙烷。同時實驗A -①、B -①中測出的四 氯乙烯與Cis、DcE均為極微量程度。計算實驗A-①、B-① 之物質平衡可知,土壤中四氯乙烯之分解量約可轉變為 71%、58%之乙烯及乙烷。 使用家畜堆肥代替下水道污泥堆肥亦可得相同的结果。 本紙乐尺度適用中國國家標準(CNS ) A4規格(210X297公釐) (請先閱讀背面之注意事項再填寫本頁) 經,ii部中次摞準為負J.消费合竹私印製 4 386 2 1 at B7 五、發明说明3fc ) 表3 使用高濃度污染土壤之脫鹵化反應試驗结果(培養55 日後) [A]甲烷生成撤生物用培養基 項目 空白組 ①埵元餓 ② FeCl2 ③ FeS〇4 ©滅菌處理 pH 5.31 7.55 4.98 6.91 7.30 0RP* 266 -288 90 -189 -47 PCESW 75 0.5 67 58 46 [B]碲酸堪原撤生物用培養基 項 目 空白組 ①适元鐵 ② FeCl2 ③ FeSCU ④滅菌處理 pH 5.31 7.19 4.89 7.39 7.36 0RP* 266 -414 109 -138 -52 PCE*- 75 6 61 51 55 單位 *〇RP(iV) wpCEUg/乾煉土 lkg) 本紙張尺度適用中 ^毕(CNS ) A4规格(2]OX 297公釐) ' 38 39498 (請先閱讀背面之注意事項再填寫本頁)Table 1 Compositions of methanogenic organisms for tapping and biodegradation composition Tap water 8 0 0 b 1 Inorganic rhenium solution 1 50m 1/1 Inorganic rhenium solution 2 50 * 1/1 Inorganic rhenium solution 1 〇ι 1/1 Vitamin solution 1 0a 1/1 NaHCOs 5. 0g / 1 Enzyme extract 1. Og / 1 Polyprotein 20 g / 1 Glucose 25 g / 1 1 Sodium citrate 25 g / 1 1 Formic acid 50n 1/1 L-cysteine gallate solution 5 0m 1/1 Na2S * 9H2〇 solution 5.0e I / 1 pH 6 · 9 ~ 7. 2 This paper size is applicable to China National Standard (CNS) A4 size (210X297 male f) 32 3 9 498 438621 A7 B7 Description of the invention (33) In the foregoing experimental conditions, the content of the content indicated by the aforementioned reaction system formula is verified 5) 2 ④ 1 As in the example, as follows. Ming: Say: S ο soiled with loam 3 For the quantity of the sample, add the table M, cover and re-glue the rubber, the base material in the rubber, and then cover and mix it. After mixing, add the soil material, base leaf, fertilizer, and humus, and use 5g of stone. 0 The piles of synbiotics and mixed micro-fertilizers, og raw dung, 1 ox and iron, og original show 1 Dinglan and show the picture 1 Test the species 7 mentioned above. The silverized atmosphere of the prepared pre-tightened paper and foil aluminum and the saturation value of the pair 7 Η 7 ′ 后 含 含 含 3 3 3 3 3 3 3 3 3 l l l l l l l l l l 2 / / The in situ display of tv-based culture microphysical micrometer C shows that the acid source of the electricity station is used to make oxygen B. The figure is shown in Figure 1X The first compartment (Please read the precautions on the back before filling this page ) Organized control of soil pollution ① The foundation is based on the cultivation and cultivation of the original protozoan acid and thiosulfur acid + + + I 8 I soil and soil pollution and contamination ②③④ Sugawara suitable for Sugawara Compatible limestone content into main A 4 g material 5 κ ο quality soil ash floc decomposing + IB heap MU cattle-based culture original 0 acid sulfur + vermiculite contamination ⑤ suspected original + mix 1. S Stucco and stone dirt combine with the soil and the limestone to form the main soil rot underwater g mud: S g Road. 0 underwater iron 0 ^ 遢. 0 1 +) -1 stone ο chemical ^ 0 Pei Chengyuan S Sulfuric acid as main acid + soil-like soil stained with soil-like soil © Soil «Rotten + This paper applies Chinese National Standard (C-NS) Λ4 regulations (210 × 297 mm) 33 3 9 498 438621 A7 B7 V. Description of the invention (34) ⑦ Contaminated soil + sulphuric acid medium 9.0 »1+ Shiyuanlang ll.〇s + mixed shell fossil fertilizer (main component shell fossil) 1.0g + sewage sludge compost 1.0g + saprophytic soil 0.5g ⑧ contaminated soil + tartarium tellurate culture medium 9.0inl + Sugawara Hungarian 1.0g + mixed calcareous fertilizer A (main ingredient limestone) 1.0g + saprolite 1. s + Rotten leaf soil 0.5 g Table 2 Composition of the components of the medium for sulphate suitable microorganisms Tap water 1 0 0 0 b 1 K2HPO4 0 + 5 g / 1 NH4C 1 1. 0g / 1 N a 2 S 0 4 1. 1.0g / 1 CaC12 · 2H2〇0. Is / 1 M g S 0 4 ♦ 7 H 2 0 2. 0g / 1 Yeast extract 1.0 g / 1 FeS〇 4 · 7H2 0 0.2g / 1 trace vitamin solution 1 0m 1/1 sodium lactate 25m 1/1 Sodium ester acid 25n 1/1 Sodium ethionate 0.1 g / 1 Ascorbic acid 0.1 g / 1 pH 6. 6 ~ 7. 0 (Please read the precautions on the back first Fill out this page} This paper size applies the Chinese National Standard (CNS) A4 specification (210X297 mm) 34 3 9498 438621 A7 __B7_ V. Description of the invention (35) The test results of Baoshi Example 1 are shown in Section 1 A second mouse. In the fourth experiment, ⑤ r ④- S test 贲 and ⑤, ④ 1 A test test B test test and ⑦'⑥. In everything. The raw material is slightly less than that of the original fertilization system a. The organic acid is not sulfur-free, and it is slightly different from the original culture of the province. This mixture is also used in combination. The knowledge of the former can be further reduced, and the cyclicity of the chlorinated chlorinated ethene is about 7 附 ρ in the loam soil. It can be used in culture and cultivation, and it can be used for cultivation. Ethylene chloride and tetrachloromethane in the environment of cyclic gas anorexia and environmental separation method are not contaminated with loam soil and the mixed iron source is only shown in Fig. 2 and _ 1 Use the second sample of chlorine, which is followed by 〇ί 〇 maleene, to obtain the gas, and then use the control system to control the powder, and use the powder to control the original lotus. Use 0) I0 (sulfur in the original truncated acid 2 and the example, application I ) Assets (I ferrochemical and loam soil contaminated by ethylene chloride four extraction plant Η A in the same phase 11 cases of implementation § Example of implementation k} 1 The same as every 0 for the test and then make the whole soil preparation, limonene Acetochlor, chlorene, and tetraethyl aeration add four or four medium-sized loam soils that are suspected of being dry loam soil (Please read the precautions on the back before filling out this page) Printed on the Central Standards Bureau of the Ministry of Economic Affairs® C Industrial Consumer Cooperatives to develop a test for the reduction of each amount of reduced ethylene,-real carbon type electrochemical CO Can be converted to K in original oxygen, then in oxygen and hydrogen, and the sum of alkane-like chloroethyl in the silver product of the extreme amount of the battery, and the amount of planene capacity is verified on the gaseous tetradecane. 0 ί 8 4 The rate of water contained in Junjie ’s test results is 0% raw ul-t. The saprophytic and defertilization of the soil extermination groups of the exhumed soil, the raw mud plain B, will be under the water. Contamination-steam in the steam ④-B-high test kettle bacteria and killing ④ phase of the product used in the Department of gas phase internal removal of the bottle sample should be taken instead of the degassing nitrogen nitrogen M acetone Inspection product M. Agaricus The paper size is in accordance with Chinese National Standard (CNS) Α4 specification (2 × 297 mm) 35 3949 8 4 3 86 2 1 at * B7 V. Description of the invention (36) Experimental conditions: A. Use of methane Formation group for forming microorganisms (Table 1) Reaction group ① Contaminated soil + methane production medium 9,0 (〇1 + 1 raw iron 1.0g + mixed calcareous fertilizer B (main components are limestone and wozhimin) 1.0g + sewage sludge 1, Og + rotten soil 0.5g ② contaminated soil + methane generation medium 9.0ml + FeC 丨 2 l.〇 s + mixed calcareous fertilizer B (main ingredient limestone and wozhimin) 1.0g + sewage sludge compost 1. 〇S + rotten soil 0.5s ③ polluted soil 堳 + methane generation medium 9,0iil + FeS〇4 1.0g + mixed Calcareous fertilizer B (main ingredient limestone and Wo Zhimin) 1.0g + sewage sludge compost 1.0g + saprophytic soil 0.5s ④ Contaminated soil of #borrowed soil + methane generation medium 9.0al + 1.0 g of burial soil + mixed calcareous fertilizer B (Main ingredients limestone and Wo Zhimin) 1.0s + sterilized sewage sludge compost 1.0g + aunt. Bacteroides rotten leaf soil 0.5g B. reaction group using lutetium tellurate culture medium (Table 2) Printed by the Consumer Cooperatives of the Central Bureau of Standards of the Ministry of Economic Affairs (please read the precautions on the back before filling this page) ① Contaminated soil + sulphuric acid medium 9.0ml + reduced iron 1.0g + mixed calcareous fertilizer B (main ingredients limestone and fertilized Min) 1.0 g + 1.0 g of sewage sludge compost + 0.5 g of saprophytic soil ② Contaminated soil + sulfuric acid into the original culture medium 9.0ml + FeClz 1, 0g + mixed calcareous fertilizer B (main ingredients limestone and Wo Zhimin) 1.0g + sewage sludge compost 1.0s + humus soil 0.5g ③ polluted soil + hafnium tellurate Original medium 9.0ml + FeS〇4 l.〇s + mixed calcareous fertilizer B (main ingredients limestone and Wo Zhimin) 1.0g + water The paper size applies the Chinese National Standard (CNS) A4 specification (210X297 mm) 36 3 9 49 8 438621 Λ7 Printed B7 by the Consumer Cooperatives of the Central Standards Bureau of the Ministry of Economic Affairs V. Invention Description (37) Road sludge compost 1.0g + humus soil 0.5g ④Contaminated contaminated soil + Sulfate medium 9.0IB1 + Suppressed iron 1. ¢) g + mixed calcareous SB material B (main ingredients limestone and wozhimin) 1.0 g + sterilized sewage sludge compost 1.0 g + sterilized saprophytic soil 0 · 5 g The results of Example 2 are shown in Tables 3 and 4. It can be seen from Tables 3 and 4 that scandium iron can decompose tetragas ethylene. In contrast, the ferrites such as F e C 1 2 and F e S 0 4 or the males of P e C1 3 cannot be decomposed. At the same time, it can be known that the mixed soil can be mixed with the original and inorganic fertilizer (pH adjuster), various kinds of piles, and the medium for methanogenic microorganisms or the medium for sulfuric acid, which can keep the soil stable and stable near PH7 The sexual environment and the anaerobic environment make the tetraethylene in the soil quickly decompose. It is also known that when FeCU or FeS04 is added to replace Korihara, the decomposition of tetrachloroethylene is almost impossible. In addition, in the case of microbial sterilization (Experiments A-④, B-④), there is only a relatively small amount of tetrahydroethylene decomposition, indicating that the method of the present invention is reducing by the multiplication of biological reactions and chemical reactions. Dehalogenation reaction Table 4 shows the analysis results of the gas components in the sample bottles in experiments A-① and B-①. It is known that a large amount of hydrogen, carbon dioxide, ethylene, and ethane can be generated in these experimental groups. At the same time, the tetrachloroethylene, Cis, and DcE measured in experiments A -① and B -① were all in a very small amount. Calculating the material balance of experiments A-① and B-①, we can know that the decomposition amount of tetrachloroethylene in the soil can be transformed into 71% and 58% of ethylene and ethane. The same results can be obtained by using livestock compost instead of sewage sludge compost. The paper scale is applicable to the Chinese National Standard (CNS) A4 specification (210X297 mm) (please read the precautions on the back before filling this page). The middle and second grades of Part II are negative. J. Consumption Hezhu Private Printing 4 386 2 1 at B7 V. Description of the invention 3fc) Table 3 Test results of dehalogenation reaction using contaminated soil with high concentration (after 55 days of culture) [A] Blank group of methanogenesis-removing medium project group ① Yuan Hung ② FeCl2 ③ FeS〇4 © Sterilization treatment pH 5.31 7.55 4.98 6.91 7.30 0RP * 266 -288 90 -189 -47 PCESW 75 0.5 67 58 46 [B] Blank group of the medium for the use of the metabolite for telluric acid ① Shimon iron ② FeCl2 ③ FeSCU ④ Sterilization treatment pH 5.31 7.19 4.89 7.39 7.36 0RP * 266 -414 109 -138 -52 PCE *-75 6 61 51 55 Unit * 〇RP (iV) wpCEUg / dried soil lkg) This paper is applicable to the standard (CNS) A4 specification (2) OX 297 mm) '38 39498 (Please read the notes on the back before filling this page)

438621 經濟部中央標準局—工消費合作社印製 A7 B7 五、發明説明(3 9 ) 即使在分解四氛乙烯之場合,亦無殘留二氢乙烯而可 Μ分解為乙烯、乙烷。 第4表 四氣乙烯在厭氣條件下脫鹵化反應時產生之氣體 (培着5 5日後) H2 C〇2 CH4 乙烯 乙烷 單 位 ml/ 乾嫌土 1 k g /iffiol / 乾燥土 1kg 空白 組 0 30 0 0 0 實驗A -① 1270 1890 trace 172 146 實驗B -① 770 1850 0 138 101 g _例3 實腌例3中使用遢原嫌為缠原劑。 在鄹接工業地區之湖泊底泥(X)及濕地之表層底泥(Y) 添加四氯乙烯,調整成最终濃度為四氯乙烯35ng /乾燥泥 lkg。在體積25公升之圓筒形不綉鋦罐(直徑330mniX高 3?0βηι)中分別裝人15kg之污染底泥成4系列之實驗組 (X區之控制組及淨化組,Y區之控制組及淨化組)。各實 驗組之條件如下。此外,為防止水份蒸散及水混人,以及 保溫之目的,各實驗容器均加Μ覆蓋。在底泥表層鋪以堆 肥或腐葉土並非必要條件,因此本實驗中不進行。將此 3區之實驗姐設於室外,再於各時間測定pH,對飽和氣化 (請先閲讀背面之注意事項再填寫本頁)438621 Printed by the Central Standards Bureau of the Ministry of Economy—Industrial and Consumer Cooperatives A7 B7 V. Description of the invention (39) Even in the case of the decomposition of tetra-aqueous ethylene, there is no residual dihydroethylene and it can be decomposed into ethylene and ethane. Table 4: Gas produced during the dehalogenation reaction of ethylene under anaerobic conditions (after 5 and 5 days of cultivation) H2 C〇2 CH4 Ethylene ethane unit ml / dry soil 1 kg / iffiol / dry soil 1 kg blank group 0 30 0 0 0 Experiment A -① 1270 1890 trace 172 146 Experiment B -① 770 1850 0 138 101 g _Example 3 In Example 3, Kashihara was considered to be a entanglement agent. Add tetrachloroethylene to the lake sediment (X) and wetland surface sediment (Y) in the contiguous industrial area, and adjust to the final concentration of 35ng tetrachloroethylene / 1kg dry mud. In a 25-liter cylindrical non-embroidery can (with a diameter of 330mniX and a height of 3? 0βηι), 15kg of contaminated bottom sediment were put into 4 series of experimental groups (control group and purification group in zone X, control group in zone Y And purification group). The conditions of each experimental group are as follows. In addition, for the purpose of preventing water evapotranspiration, water mixing, and heat preservation, each experimental container is covered with M. Spreading compost or rotten soil on the surface of the sediment is not necessary, so it will not be performed in this experiment. Set up the experimental sister in this 3 area outdoors, and then measure the pH at each time to saturate the gas (please read the precautions on the back before filling this page)

本紙張尺度適用中國國家標準(CNS ) A4規格(210X297公釐) 39 39498 Λ7 438621 _ B7 五、發明説明(40 ) 銀電槿之氧化還原電位、四氣乙烯之滅少盪。實驗期間中 室外溫度範圍為7〜18T,底泥含水率約41〜50%。 (請先鬩讀背面之注意事項再填寫本頁) (實驗條件) X區控制組:污染底泥+纯水3000ml X區淨化組:污染底泥+啤酒糖化酒粕廢水3200ml +堪原 鏃500g+混合石灰質肥料B (主成份石灰石 及沃植敏)500g +下水道污泥堆肥500s +腐 絮土 250g Y區控制組:污染底泥+純水3300mi Y匾淨化組:污染底泥+啤酒糖化酒粕廢水3500*1+遢原 鐵500g+混合石灰質肥料B (主成份石灰石 及沃植敏)500g +下水道污泥堆肥500g +腐 葉土 2 5 0g 其中啤酒耱化酒柏廢水之主成份為遢原糖96〇〇w/l, 醋酸 180ng/l,乳酸 3100ag/l,懸浮物質 8100mg/l, BOD(生物化學需氧量)12700Bg/ 1,及總有機碳濃度5100 a ε / 1 〇 經濟部中央標隼局員工消費合作社印製 四氯乙烯濃度變化之结果示於表5。pH及對館和氛化 銀電極之氧化堪原電位,X區控制組及Y區控制組均為 PH4.6〜5.3, 0RP為180〜300mV程度,X區淨化組及Y區 淨化組均為PH7〜7.4、 0RP- 400〜- 570bV,由其中可知, 無論X區淨化組、Y區淨化組之四氣乙烯均可由本發明之 淨化方法有效加Μ分解。 本紙張尺度適用中國國家標準(CMS ) Α4現格(210X297公釐) 40 3949 8 經碘部中次標準局負工消費合作社印裝 39498 4 3 862 1 at ______B7 五、發明説明<« ) 第5表 底泥中四氣乙烯濃度之變化 (單位:mg/乾煉泥lkg) 第0曰 第19日 第28日 第40日 第57日 X匾控制组 33 30 28 29 30 5{匾淨化組 28 9.3 5.9 2.7 1.8 Y匾控制組 35 28 30 27 29 Y區淨化組 31 16 10.6 6 . 1 3.3 本發明中,由化學反應结合生物性厭氣反應,可以快 速、簡便地淨化土堳、下水道水等因鹵化有機化合物污染 之污染物。同時,本發明之方法,淨化時污染物中不致於 溶解出鹵化有拥化合物。例如污染土壤等之場合,只要保 持該污染土壤等的缠當保水性,即可K加K淨化而不致於 使該歯化有櫬化合物之汚染滲透入較污染位置更深之地下 〇 本發明可以將鹵化有機化合物轉變為乙烯或乙烷之類 不含氯有機化合物,反應中無有害的中間產物殘餘,因此 無有害中間產物積存之問題發生。 奮掄例4 實施例4中使用埋原鐡或生锇_為堪原劑《 實施例4之四氛乙烯土壤淨化實驗中,使用表6所示 的申烷生成微生物用培着基。同時,實_例4中所示的氣 張尺度適用中國國家標準(CNS ) A4規格(2丨OX297公釐) 41 (請先閱讀背面之注意事項再填寫本頁)This paper size applies the Chinese National Standard (CNS) A4 specification (210X297 mm) 39 39498 Λ7 438621 _ B7 V. Description of the invention (40) The oxidation-reduction potential of silver electric hibiscus and the elimination of four-gas ethylene are less volatile. During the experiment, the outdoor temperature range was 7-18T, and the moisture content of the sediment was about 41-50%. (Please read the precautions on the back before filling this page) (Experimental conditions) X zone control group: polluted bottom mud + 3000ml of pure water X zone purification group: polluted bottom mud + beer saccharified wine meal wastewater 3200ml + kanbara tincture 500g + mixed Lime Fertilizer B (main ingredients limestone and Wo Zhimin) 500g + sewage sludge compost 500s + humus soil 250g Y zone control group: polluted bottom mud + pure water 3300mi Y plaque purification group: polluted bottom mud + beer saccharified wine meal wastewater 3500 * 1 + 500 g of Liaoyuan iron + mixed lime-lime fertilizer B (main ingredients limestone and Wo Zhimin) 500 g + sewage sludge compost 500 g + rotten leaf soil 2 5 0 g Among them, the main component of beer puppet vineyard wastewater is Liaoyuan sugar 96〇〇w / l, acetic acid 180ng / l, lactic acid 3100ag / l, suspended matter 8100mg / l, BOD (Biochemical Oxygen Demand) 12700Bg / 1, and total organic carbon concentration 5100 a ε / 1 〇 Employees ’consumption The results of the changes in the concentration of tetrachloroethylene printed by the cooperative are shown in Table 5. The pH and oxidation potential of the hall and the oxidized silver electrode are both pH 4.6 ~ 5.3 in the X-zone control group and the Y-zone control group. PH7 ~ 7.4, 0RP- 400 ~-570bV, it can be known that the four gas ethylene in the X-zone purification group and the Y-zone purification group can be effectively decomposed by the purification method of the present invention. This paper size is applicable to the Chinese National Standard (CMS) A4 (210X297 mm) 40 3949 8 Printed by the Sub-consumer Cooperative of the Intermediate Standards Bureau of the Ministry of Iodine 39498 4 3 862 1 at ______B7 V. Description of the invention < «) 5 Changes in the concentration of four gas ethylene in table bottom mud (Unit: mg / dried sludge 1kg) Day 0: Day 19, Day 28, Day 40, Day 57 X Plaque Control Group 33 30 28 29 30 5 {plaque purification group 28 9.3 5.9 2.7 1.8 Y plaque control group 35 28 30 27 29 Y zone purification group 31 16 10.6 6. 1 3.3 In the present invention, the chemical reaction combined with the biological anaerobic reaction can quickly and easily purify soil water and sewer water Pollutants contaminated by halogenated organic compounds. At the same time, the method of the present invention does not dissolve halogenated compounds in the pollutants during purification. For example, in the case of contaminated soil, as long as the conserved water retention of the contaminated soil is maintained, K plus K purification can be performed without causing the contamination of the tritiated compound to penetrate deeper into the ground than the contaminated site. Halogenated organic compounds are converted into chlorine-free organic compounds such as ethylene or ethane, and no harmful intermediate products remain in the reaction, so no problem of harmful intermediate products occurs. Example 4: Buried raw mash or raw mash was used as the kangen agent in Example 4. In the four-smooth ethylene soil purification experiment of Example 4, the stilbene-forming microorganism bases shown in Table 6 were used. At the same time, the tension scale shown in Example 4 applies the Chinese National Standard (CNS) A4 specification (2 丨 OX297 mm) 41 (Please read the precautions on the back before filling this page)

4386 2 1 ;; 五、發明説明(42 ) 化邐原電位,為使用白金電極為金属電極,使用飽和氯化 銀電極為比較電極測定所示之電位。 表6 甲烷生成微生物用培養基 成分 添加量 自來水 880ml 無機塩溶液1 5 Obi 1 / 1 無機塩溶液2 50m 1 / 1 無機塩溶液 10b 1 / 1 维生素溶液 1 Oi 1 / 1 NaHC〇3 5 . 0g/ 1 酵母萃取物 1 .0g/ 1 聚蛋白陳 2 . 0g/ 1 萄萄糖 2 . 5g/ 1 撺撵酸納 2 . 5g/ 1 甲酵 50a 1 / 1 半胱胺酸塩酸塩 0 . lg/ 1 R a 2 S * 9 Η 2 0 0 . lg/ 1 pH 6 . 9 〜7 . 2 經濟部中央標準局員工消費合作社印裂 (請先閲讀背面之注意事項再填寫本頁) 淨化實驗A工廠採取之四氯乙烯污染土壤(污染濃度 為對lkg乾煉土壤,土壤中所含的四氯乙烯為25ig>。 實驗先以125nl容量之樣品瓶採取30g之污染土壤,再 本紙張尺度適用中國國家標準(CNS ) A4規格(210X297公釐) 42 394 98 438621 經濟部中央標準局員工消費合作社印製 Λ7 B7五、發明説明(43 ) MM下所示的條件將甲烷生成微生物培養基、還原鐡或生 戡屜、下水道污泥堆肥混合後,潮定四氯乙烯之分解。土 壤中通原搛、生嫌屑、下水道污泥堆肥之添加量為5% (重 量)。生餓屑則過篩分級,粒徑500wmM下者為生鐵屑A, 5 0 0〜8 0 0 πι為生戡屑B , 8 0 0// m以下為生鐵屑C。同時, 樣品在調整時均K氮氣取代樣品瓶之氣相部份。 土壤淨化時土壤內水份含水率為48.4〜48.9%。此處 所詡的含水率(%)係以(水份重量/濕潤土壤重量)X100 所求得之值。 實驗培養60日。再測定土堳中pH、對飽和氯化銀竃極 之氧化還原電位、四氢乙烯滅少量、及氣相部份中乙烯、 乙烷產生量、S氣、二氧化碳、甲烷生成量。 此處使用的堪原嫌,使用如上述之市售和光純藥公司 之1级埋原嫌粉。 窗驗條件 ① 污染土壤30g(控制組、比較例) ② 污染土壤30g +甲烷生成用培養基9.0ml +還原嫌1.5s + 下水道污泥堆脃1.5g ③ 污染土壤30g +甲烷生成用培養基9.0b1+生鐵屑A 1.5g +下水道污泥堆肥1.5g ④ 污染土壤30g +甲烷生成用培養基9.0bi1+生锇屑B 1.5s +下水道污泥堆肥1.5g ⑤ 污染土壤30g +甲烷生成用培養基9.0ml +生嫌屑C 1.5g +下水道污泥堆肥1.5g_ 本紙張尺度適用中國國家標準(CNS ) A4規格(210X2W公犛) " 43 39498 (婧先閲讀背面之注意事項再填寫本頁) Λ7 B7 43 86 2 1 五、發明説明(44 ) 實施例4之試驗結果示於表7、表8。 (請先閱讀背面之注意事項再填寫本頁) 表7所示為以生鐵屑等淨化的場合,土壤中四氨乙烯 之濃度。 表8所示為以生鐵屑等淨化土壤中四氯乙烯時產生的 氣照。 表7 生嫌屑等對土壤中四氢乙烯之淨化结果 (培養6 0日後) 土壤中PCE (g / 乾燥土 1kg) pH ORP (mV) ①污染土壤(控制姐) 23 6.63 307 ②還元嫌+堆肥 0 7 . 58 -537 ③生鐮靥A+堆肥 0 7.27 -375 ④生嫌屜B +堆肥 16 7.25 -229 ⑤生嫌i騸C +堆肥 20 7 . 27 -225 經濟部中央標準局員工消費合作社印製 本纸張尺度適用中國國家標準(CNS ) A4規格(210X297公釐) 44 3 94 98 4 3 B 6 2 1 A7 B7五、發明説明Us ) 表8生嫌屑等對土壤中四氣乙烯淨化時之氣«產生量 (培養60日後) PCE之乙稀、乙烷 轉換率(⑹ Η2 (nl/kg-±) CH4 {l/kg-±) c〇2 (ml/kg-i) ①污染土壤(控制組) 0 0 0 trace ②還元鐵+堆肥 79 3.4 trace 190 ③生鐵屑Α+堆肥 73 2.3 〇 243 ④生賴屑Β+堆肥 25 1.6 〇 366 ⑤生嫌屑C+堆肥 7.6 1.8 〇 414 同時,表7中所表示之「土壤中四氢乙烯(PCE)、pH 、0RP」為培養60日後之值。表8中所表之「四氯乙烯 (PCE)之乙烯、乙烷轉化率」為培養60日內四氯乙烯轉化 為乙烯、乙烷之比例。「H2、CH4、C〇2j各表每lkg乾燥 土壤在各期間内所產生氣髓之量。 使用埵原擞之組及使用生鐵屑A之組,土壤中四氯乙 烯可Μ淨化至無法檢測出的程度。 同時可知使用生辨屑與遢原嫌同樣,四氫乙烯可Μ脫 氯而轉化為乙烯、乙烷。尤其是使用生截屑A,亦即粒徑 小之生戡屑時,四氯乙烯可Μ極為有效地脫氛。 Μ生锇屑淨化污染土壤中四氛乙烯之場合.土壤可以 維持在ΡΗ7.2〜7.3之中性t及對飽和氛化銀轚極之氧化堪 本紙張尺度遴用中國國家標準(CNS ) A4規格(210X297公f ) 4 5 3 9 498 — — —— —— —— 01 — . 4 (請先閲讀背面之注意事項再填寫本頁) ^38621 經濟部中央標準局負工消費合作社印製 ΑΊ Β7五、發明説明(46 ) 原電位為- 225〜375nV之《原性瑁境。因此,比較使用遢 原鐵之土壤淨化法及使用生鐵屑之土壤淨化法,兩者之土 壤環境可說是無所差異。 此外,添加甲烷生成用撤生物培養基之②③④及⑤姐 ,均在揉品瓶之氣相部份有二氧化碳產生,因此應該有撤 生物生長。亦即可Μ說生鐵1為對土壤微生物生長無害的 物質。 管油ί俐5 先調製與實SIS例4同樣之四氱乙烯污染土壤或另再添 加成四氯乙烯含量不同之污染土壤樣品。如此,可得到換 算1 k g之乾嫌土壤,土壤中四氣乙烯含5 0 m g之污染土壤、 含7 5 m g之污染土壤,及含1 4 0 m g之污染土壤。再對各污染 土壤進行淨化試驗。 實驗同實施例4 ,以1 2 5 m 1容量之樣品瓶秤取3 0 g之污 染土壤,再以表6之甲烷生成用培養基9.0ml、粒徑 500wai以下的生鐵屑A 1.5g、下水道污泥堆肥1.5g混合, 測定四氯乙烯之分解。同時,樣品在調製時樣品瓶之氣相 部份均Μ氮氣取代。 實驗係在室溫下持縯培養,測定63日後土墉中pH、對 飽和氯化銀電極之氧化堪原電位、四氯乙烯之減少量、Μ 及氣相部份乙烯、乙烷之生產量。 實.驗條件 ① 污染土壤(5 S四氛乙烯/ kg乾煉土壤)30g(控剌組) ② 污染土壤(50ag四氢乙烯/ kg乾燥土壤)30S +甲烷生成 (請先閱讀背面之注意事項再填寫本頁) 本紙張尺度適用中國國家標準(CNS ) A4規格(2丨0X297公釐) 46 3 9 4 9 8 經濟部中央標準局員工消費合作社印製 4 3 8 6 2 1 A7 B7 五、發明説明(47 ) 用培養基9.0ml +生羝盾A 1.5g +下水道污泥堆肥1.5s ③ 污染土壤(75ng四氯乙烯/kg乾嫌土壤)30g (控制組) ④ 污染土壤(75iag四氛乙烯/ ks乾煉土壤)3〇s +甲烷生成 用培養基9.0m丨+生截MA 1.5g +下水道污泥堆肥1.5g ⑤ 污染土壤(140 ng四氛乙烯/ kg乾燥土堳)30g (控制組) ⑥ 污染土壤(140ms四氣乙烯/ kg乾煉土堳)30g +甲烷生成 用培養基9.0»1+生嫌屑A 1.5g +下水道污泥堆肥1.5g 實施例5之試驗結果示於表9。由此表可知,換算lkg 乾嫌土墉之土壤中含四氣乙烯量為50bS、75ns、 140ns比 例之高濃度污染土壤,可Μ使用粒徑500ϋΐ®以下之生撖屑 Α脫氣為乙烯、乙烷,顯示本土壤淨化法之有效性。此土 壤淨化實驗中,四氯乙烯之分解產物僅有氣相中及土壤中 有撤量之三氣乙烯及cis-DCE產生,幾乎無法澜得氯化乙 烯。 此外,使用生鐵屑A淨化因高濃度四氯乙烯污染之土 壤,土壤中可K安定地維持在PH7.2〜7.3之中性、及對飽 和氣化銀電極之氧化遢原電位為-350〜3 80 i»V之《原性環 境。 表9中所表之「土壤中四氛乙烯、pH, 0RP」為培養 63日後之值。表9中所表之「四氯乙烯之乙烯、乙烷轉變 率」為培養63日後四氯乙烯轉變為乙烯、乙烷之比例。 (請先閱讀背面之注意事項再填寫本頁) 本紙張尺度適用中國國家標準(CNS ) A4規格(2! 0 X 297公釐) 3 9 49 8 經潢部中泱標準局負工消費合作、ϊι印$; 4386 2 1 at B7 五、發明讀明(姑) 表9生嫌曆對高潫度四氛乙烯污染土壤之淨化结果 (培養63日後> 土壤中PCE (ag-PCE/ kg-乾嫌土 1 PCE之 乙烯、乙烷 轉換率(%) pH 0RP (mV) ①污染土壤(控制組) 45 0 6.71 360 ②生截屑Α +堆肥 4.0 65 7.28 -380 ③污染土壤(控制組) 73 0 6.75 345 ④生鐵屑Α+堆肥 19 58 7.19 -375 ⑤污染土壤(控制組) 139 0 6.86 336 ⑤生鐵屑Α+堆肥 78 28 7.31 -347 (讀先閱讀背面之注意事項再填寫本頁) 本紙張尺度適用中國國家標準(CNS ) Α4規格(210Χ297公沒) 39498 43 86 2 1 at Β7 五、發明説明(49 ) 由此可知本發明中使用生嫌粉末或堪原嫌粉末之金屬 粉末,可以對低濃度至高濃度廣泛之污染湄度範園氯化有 機化合物達成高度之淨化率。亦即使用例如生锇屑之生嫌 ,可低成本、安全旦簡單之處理糸铳淨化因氯化有楗 化合物污染之污染物.且可有效利用產業廢棄物。 此外.结合低溶解性土壤改良劑可以防止該污染土壤 中溶出氛化有機化合物。同時,保持該污染土壤遽當之保 水性時,淨化可Μ達成且可維持已在地下中生成之有機氯 化合物污染不會自污染位置擴大滲透至更深之深度。 窨油?俐fi 實施例6對應本發明之第2態樣。實豳例6顯示,即 使在不添加從觴曾養型厭氣性微生物之曾養源的場合,亦 可Μ分解鹵化有機化合物。 比較使用四棰類之适原則:(1)金屬鐵(比較例)、(2) 錳(3)鋁一矽合金、(4)次磷酸納。 各還原劑之標準電極電位乐於表10。 表10 适原劑之檷準電搔電位 (請先閱讀背面之注意事項再填寫本頁) 經濟部中央標準局員工消費合作社印製 堪原劑 檷準電極電位UV) (1)金國嫌 -440 (2)錳 -1180 (3)鋁一矽金合 -1600 (4 )次磷酸納 -499 本紙張尺度適用中國國家標導(CNS ) Α4規格(2丨0Χ 297公釐) 49 3 9 4 9 8 Λ7 4 3 86 2 1 __B7 五、發明説明(5 0 ) 將(1 )金驅嫌2 0 g、 ( 2 )錳1 0 g、 ( 3 )鋁一矽合金1 、及 (請先閱讀背面之注意事項再填寫本頁) (4)次磷酸納20g之還原劑添加於6500g(含水率60% )含四 氣乙烯1 5 0 » g / k g壤土質土壤中,維持在2 0 〇下,測定其 後之狀態。 (2)及(3)在1小時内氧化邐原電位降低至- 500jiV以下 ,其後10日中即可維持在-500bVM下。四氯乙烯在10日後 可K完全地脫鹵化為乙烯、乙烷。(4)在1小時內氧化堪 原電位降低至-450mVM下,其後10日即雄持在-450n\iM下 。四氛乙烯在10日後完全脫鹵化成乙烯、乙烷。相對地, (1) 之氧化埵原電位降低至_400bV須時5日,其後5日則 維持為- 400bV。四氯乙烯在10日後仍只有2成脫鹵化至乙 烯、乙烷。 奮撫俐7 比較(1)僅添加遢原劑,且不添加有櫬碳源之組.及 (2) 添加适原劑及有機碳源之組,在此之适原劑使用鈣一 矽合金(搮準電極電位-1900mV),有機碛源則則使用醏酸 納。 經濟部中央標準局員工消費合作社印製 (1)及(2 )中.對吸有三氯乙烯2 0 0 m g / k g之粘土質土 壤65kg(含水率55%)添加100g之鈣-矽合金。(2)中,對 此再添加70g之醋酸納及7s之其他營養源。各組維持於 2 溫度,再測定其後之狀態。 (1)、 (2)均在1小時內氧化适原電位即降低至 以下。(1)之氧化還原電位在10日中維持在_500bVM下· 之後即徐徐轉變成氧化狀態,至40日之間氧化适原電位上 本紙浪尺度適用中國國家標準(CNS ) A4規格(210X 297公釐) 50 39498 43862 t A7 ______五、發明説明(Si ) 昇至OmV。三氯乙烯有8成遒原成乙烯、乙烷,另有2成 餘留於土堳中。相對地,(2)在40日内維持氧化遨原電位 在- 500nVM下,三氛乙烯有99%堪原為乙烯、乙烷。 本發明之堪原劑,由於表面不易包覆安定的氧化膜, 且不易溶解於水,因此易與污染物接觸.提高分解速度。 此外,B染物為粘土質土壤或結塊之粉土質等底透水性物 質時,再配合有櫬碳源為撤生物生長基質亦可進行脫鹵化 反應。 (請先閲讀背面之注意事項再填寫本頁) 經濟部中央標準局員工消費合作社印製 比 較 使 用 (1)金羼戡粉末 (控_組)、 (2 )次磷酸納粉末 Ή 或 (3)撺樺酸鈦水溶液為堪 原劑。 實 m 條 件 使 用 換 算 乾 煉土為含四氯乙烯120k g/ kg之壤土質土 壤 〇 初 期 時 氧 化 堪原電位為+ 350mV, 土 壤量為100b3。 輪 結 果 ( 2), (3 )在1 小時內氧化 缠原電位降低至- 4 5 0 nVK下 , 其 後 5 曰 内 雄 持為-450b VM下。四氯 乙稀則在5日後完 全 脫 鹵 化 成 乙 烯 、乙烷。 相 對 地 1 (1 )組使用1台 倒结機在1 0曰内才將土壤與 金 屬 混 拌 完 全 > 之後尚須5 E 丨才將氧化 堪原電位降至 — 4 0 0 m V , 其後5 日則維持在 - 4 0 0 bV以下。四氯乙烯在 20 曰 後 有 2 成 脫 鹵化為乙烯、 乙烷。 實 腌 例 9 各組均使用抗壤血酸為運原劑。(1)組中不添加有機 本紙張尺度適用中國國家標準(CNS ) A4規格(210X297公漦) 5 1 3949 8 A7 438621 B7 五、發明説明(52 ) 碳源。相對地,(2)組中使用醏酸納為有機碳源。 (請先閱讀背面之注意事項再填寫本頁) 使用換算乾煉土為含四氱乙烯lOOng/ks之粘土。初 期之氧化理原電位為+32〇1^,初期?11為6.5。 W路结果 (1)、 (2)組均在注入缠原劑後1小時内其氧化通原電 位降至+130mVM下。(1)在10日中氧化堪原電位維持在 + 130bVM下,之後摄媛轉變為氧化狀態,40日後氧化埋原 電位漸上昇為+3 00 »^。卩11則由第0日之6.3漸漸降低為 40曰後之5.5,四氣乙烯則5成被堪原成乙烯、乙烷,另 有5成餘留於土壊内。 相對地,(2)在其後氧化通原電位漸渐降低,至20日 後為-150mVM下,維持至40日後為-150nVM下。pH則由第 0日之7.5漸渐降低至40日後為6.8。四氯乙烯有99.9%通 原為乙烯、乙烷。 此實腌樣態使用之遢原繭為水溶性,因此因_化有機 化合物污染之污染物可以與堪原劑接觸,促進堪原性脫南 化反應。 好硪部中央標隼局員工消资合作社印" 此實驗搛態使用之遢原劑,其檷準電極電位輿金羼嫌 為同等或在其Μ下,因此,具有與鹵化有機化合物電位差 大,因而可加速脫鹵化之優點。此外,污染物為粘土質土 壤及结塊之粉土質等低透水性物質時,亦可配合微生物生 長基霣之有機碳源而進行脫鹵化反應。同時,此些遢原劑 亦不Μ金屬嫌無鈍態化。 窗淪例1 〇 本紙張尺度適用中國國家標準(〇«)/\4規格(210:>< 297公1) 52 39 498 43 86 2 1 A7 __B7五、發明説明(5 3 ) 本發明顧示可Μ分解鹵化芳香族化合物。 將20g之金層鐵添加於五氯酚(以下簡稱PCP)濃度 lOiag/ks之6s壤土土壤中。10-1組中另再添加1公升表11 中所示之硝酸堪原性撤生物用培養基。相對地,10-2組為 控制組,只添加1公升水。 表11 硝酸适原性橄生物用培養基 成 分 添加量 鉀 4.5g/ 1 醋酸鉀 8.5g/ 1 碳酸氫納 5.0g/ 1 六水和氛化鎂 0.2g/ 1 酵母抽出物 0. 1 g/ 1 稀釋水 自來水 pH 6 . 9 〜7 . 4 (請先閱讀背面之注意事項再填寫本頁) .ο 丁 --5 鈔漭部中决椋準局負h消費合作社印$, 其次,混拌後維持於281C,再測定PCP濃度及產物濃 度之變化。結果示於表12及表13。 本紙張尺度適用中國囤家標準(〔-!^)八4規格(210乂 297公釐) 3 9 4 9 8 43 86 2 1 at B7 五、發明説明(54 ) 表12: 10-1姐之結果 化合物名 0曰後 20日後 40日後 ? C? (mg / kg) 10.1 0.58 0 . 0 1 ^ TeCPiffig/ kg) 0.00 2 . 0 0.00 C P( η g / kg) 0.00 2.3 0.02 Phenol 0.00 1.2 3.1 Eh (aV) + 312 -380 -423 表13 :10-2組 之结果 化合物名 0曰後 20日後 40日後 PCP (丨g / kg) 10.2 2.4 0.9. TeCPfmg / kg) 0.00 1.0 0.00 CP (ig/ kg) 0.00 2.1 2.8 Phenol 0.00 0.8 1.0 Eh(aV) + 308 -1 70 + 118 结濟部中决標準局妇工消费合作社印^ (請先閱讀背面之注意事項再填寫本頁) -〇, 表12及表13中TeCP及CP各表示2,3, 5,6-四氛酚及3-氛 酚。同時,Eh為換算為對標準氫電槿之標準電槿電位之值 0 比較例10-1姐及10-2組可知,五氛酚可以快速分解。 本紙張尺度適用中國國家標準(CNS ) Λ4规格(210X 297公釐) 54 3 9498 438621 B7 烀濟部中次標準局員工消资合竹社印繁 五、發明説明(55) 1 1 10 -1組 中 五 氯 酚 應 該 是 經 由 2,3, 5 , 6- 四 氛酚及 / 或 3- 氯 酚 ί 1 I 而 分 解 為 鼢 同 時 2 , 3, 5, 6 - 四 氯 酚 及 3-氯酚 m 該 可 再 分 1 ! I 解 為 其 他 之 化 合 物 0 1 | 請 I I 直 羞 JL1 閱 1 I 讀 1 | 實 W 例 1 1主 要 對 應 本 發 明 之 第 3 態 樣。 背 之 1 I 實 施 例 1 1中 使 用 表 1 4之 氧 化 態 氮 堪 原用撤 生 物 培 養 基 注 意 事 及 表 15之 甲 焼 生 成 微 生 物 用 培 養 基 (控制組)淨 化 四 氛 乙 院 項 1 填 Λ 污 染 土 埔 〇 表 1 4之 培 養 基 組 成 中 氧 化 態 氮相當 於 有 機 態 碳 本 頁 W 1 之 23重 量 % 〇 淨 化 實 驗 在 室 溫 (12〜23C >下實施30日 1 測 1 i 1 定 土 壤 各 性 質 之 變 化 記 於 表 1 6中 〇 1 1 pH之 測 定 則 調 製 土 壤 纯 水 = 1 : 1 (w t), 再 以 東 亞 電 1 波 工 業 製 pH計 HH -5 B型測定。 對飽和氯化銀電極之氧化适 iT I 原 霣 位 (0RP)之測定, 以調製之土壤: 無氧水= =1 1 ( w t), 1 I 將 中 央 科 學 製 0RP計 UK- 20 3 0 電 極 浸 入 且 放置30分鐘 後 測 定 1 I 〇 再 者 , 本 實 施 例 中 所 示 的 對 飽 和 氣 化 銀電極 之 氧 化 通 原 r1) 電 位 » 為 白 金 電 極 之 金 屬 電 槿 9 使 用 飽 和氯化 銀 電 棰 為 比 [y.J I 較 極 則 定 所 顯 示 之 罨 位 〇 土 壤 氛 化 乙 烯類之 分 析 則 依 據 1 1 曰 本 横 濱 國 立 大 學 開 發 之 方 法 (宮本健- -等、 「土壤低沸 1 1 點 鹵 化 有 機 化 合 物 含 量 之 拥 定 方 法 J 水環境 學 會 誌 » 1 1 1995 年 第 1 8卷 * 第 6 號 9 477〜488頁 ),以乙酵萃取後 1 I 轉 變 為 癸 院 再 Μ 曰 立 氣 相 層 析 儀 G- 5000型.F ID檢測器、 1 | 20% TCP c h Γ 0 IQ 0 SO r b WAV DHCS 60 -80 a e s h 管 柱 分 析 0 氣 I 1 i 相 中 產 生 之 氫 氣 % 二 氧 化 碳 > 甲 烷 氮 氣之澜 定 1 則 使 用 1 1 GL科學型氣 相 磨 析 儀 G C - 3 20 型 TCD檢測器、A c t i v e 1 1 本紙張尺度適用中國國家標準(rNS ) A4規格(210X297公釐) 55 3 9 498 4 3 8 6 2 1 Λ7 Β7 五、發明説明(56 ) carbon 30/ 60或Molecular sieve 13X。 土壤中确酸態氮 、亞硝酸態氮離子濃度則Μ日立陰離子層析儀2010i測定 土壤:純水=1: l(wt)調整之萃取水。 表14 氧化態氮還原用撤生物培養基 (請先閱讀背面之注意事項再填寫本頁) 成 分 添加量 硝酸鉀 4 . 5g/ 1 醋酸鉀 8 . 5 g / 1 碳酸氫納 5 . 0g/ 1 六水和氯化鎂 0.2g/ 1 酵母抽出物 0. 1 g/ 1 稀釋水 自來水 pH 6 , 9〜7 . 4 經濟部中央標準局員工消費合作社印製 表15 甲烷生成微生物培養基 成 分 添加量 L-半胱胺酸塩酸塩 0 . 1 g/ 1 聚蛋白陳 2 · 0g/ 1 葡萄糖 2 * 5 g / 1 擰樣酸納 2.5g/ 1 甲醇 5 . 0m 1 / 1 碳酸氫納 5.0g/ 1 九水和硫化納 0. 1g/ 1 酵母萃取物 1.0g/ 1 稀釋水 自來水 pH 6 . 9〜7 . 2 本紙張尺度適用中國國家標準(CNS ) A4規格(2丨0X2?7公釐) 56 3949 8 43 86 2 1 經 浪 部 中 標 準 局 員 j- 消 f 合 作 社 印 A7 B7 五、 發明説明( 57) 1 1 淨 化 η 驗 Μ化學 工 廠 採 取 的 四 氣 乙 η 污 染 土 壤 ( 染 ! | 濃 度 約 2 5 n t k g乾嫌 土 壤 ) η 拖 寶 驗 中 以 搜 廣 Μ I 之 樣 1 I 品 瓶 秤 取 30g之 污染 上壤 再 VX 下 所 的 降 牛混 含培 善 請 1 1 | 基 > 金 靥 粉 末 經 30曰 後 测 定 白 四 氯 乙 烯 分 解 之 土 壤 各 性 質 A 閣 讀 1 1 ! 之 變 化 狀 態 等 ( 表.1 6) 〇 金 靥 粉 末 則 使 用 和 光 純 m 製 之 1 级 背 1¾ 之 Γ 還 原 m 粉 末 〇 同 時, 鋼 製 樣 品 時 Μ 氦 取 代 樣 品 瓶 之 氣 體 部 5. 意 畜 份 〇 Ύ 項 再 1 4 S. 旃 條 件 本 W 頁 1 ① 污 染 土 壤 30 ε 、_<·· 1 I ② 污 染 土 壤 30 Ε +水S .0〇] + m 原 嫌 0 07 g 1 1 ③ 污 染 土 壤 30 g +氧化態氮通原用撤生物培養基90ml- !堪 1 1 訂 原 嫌 0 . 07 S 1 ④ 污 染 土 壤 30 δ ♦甲烷生成微生物用培養基9 .0 B1 1 + 遢 原 锇 i 1 0 . 07 g I I 實 驗 结 果 示 於表 1 6 〇 可 以 確 定 t 在 使 用 氧 化 態 氮 m 原 r\ 培 養 基 之 埸 合 9 不僅 四 氣 乙 烯 可 脫 氯 形 成 乙 烯 及 乙 1 且 j 可 抑 制 土 壌 黑 變 及甲 烷 產 生 > 硫 酵 糸 臭 氣 之 發 生 〇 同 時 可 I I I 發 現 » 產 生 之 氮 氣可 Μ 稀 釋 產 生 的 氫 氣 0 此 外 亦 未 發 現 土 1 i 壤 中 殘 存 氧 化 態 氮、 亞 氧 化 態 氮 0 1 1 另- 1方面, 只添加金屬及水之組則ρ Η大幅降低, 對飽 I 1 和 氛 化 銀 電 極 之 氧化 通 原 電 位 在 30 曰 後 亦 升 高 為 + 2 mV > 因 1 1 此 無 法 充 份 堪 原 脫氣 分 解 0 因 此 其 結 果 有 — 部 份 之 四 氯 乙 1 1 烯 仍 餘 留 於 土 壤 中. 對 乙 烯 之 轉 化 率 僅 有 26% 〇 此 顯 示 » 1 1 | 只 添 加 金 屬 粉 末 之組 難 Μ 長 期 間 維 持 逋 當 的 還 原 狀 態 * 惟 1 1 本紙張尺廋適用中國國家標準U、NS ) Λ4現格(210X2W公釐) 57 3 9 4 9 8 f 438621 A7 B7五、發明説明(58)4386 2 1 ;; 5. Description of the invention (42) The potential of the lutetium is measured by using a platinum electrode as a metal electrode and a saturated silver chloride electrode as a comparison electrode. Table 6 Addition amount of methanogenic microorganism culture medium Tap water 880ml Inorganic rhenium solution 1 5 Obi 1/1 Inorganic rhenium solution 2 50m 1/1 Inorganic rhenium solution 10b 1/1 Vitamin solution 1 Oi 1/1 NaHC〇3 5. 0g / 1 Yeast Extract 1.0g / 1 Polyprotein 2 2.0g / 1 Glucose 2.5g / 1 Sodium gallate 2. 5g / 1 Formazan 50a 1/1 1 Cysteine gallate 0. lg / 1 R a 2 S * 9 Η 2 0 0. Lg / 1 pH 6.9 ~ 7.2 2 Printed by the Consumer Cooperatives of the Central Standards Bureau of the Ministry of Economic Affairs (please read the precautions on the back before filling this page) Purification Experiment A Factory Contaminated soil with tetrachloroethylene (contamination concentration is 1kg dry soil, 25ig > in the soil. In the experiment, 30g of contaminated soil was used in a 125nl sample bottle, and the paper size is applicable to China Standard (CNS) A4 specification (210X297 mm) 42 394 98 438621 Printed by the Consumers' Cooperative of the Central Bureau of Standards of the Ministry of Economic Affairs Λ7 B7 V. Description of the invention (43) The conditions shown in MM will generate methane microbial culture medium, reduce tritium or produce After mixing the compost and sewage sludge, Determining the decomposition of tetrachloroethylene. The amount of compost in the soil, raw crumbs, and sewage sludge compost is 5% by weight. Raw crumbs are sieved and classified. The diameter of 500wmM is pig iron scrap A, 5 0 0 ~ 8 0 0 π is raw swarf chip B, and below 80 0 // m is pig iron chip C. At the same time, the sample is adjusted by K nitrogen to replace the gas phase part of the sample bottle. Water in the soil during soil purification The moisture content is 48.4 ~ 48.9%. The moisture content (%) here is the value obtained by (water weight / wet soil weight) X100. Experiment culture for 60 days. Then measure the pH in the soil and measure the saturated chlorine The redox potential of the silver halide pole, the small amount of tetrahydroethylene, and the amount of ethylene, ethane, S gas, carbon dioxide, and methane produced in the gas phase. The first-class burying of the original powder was sold by Wako Pure Chemical Co., Ltd. Window inspection conditions ① 30g of contaminated soil (control group, comparative example) ② 30g of contaminated soil + 9.0ml of methane production medium + 1.5s of reduction + + 1.5 of sewage sludge pile g ③ 30g of contaminated soil + 9.0b1 of methane production medium + pig iron scrap A 1.5g + sewage sludge 1.5g of fertilizer ④ 30g of contaminated soil + 9.0bi1 of methane production medium + raw crumbs B 1.5s + sewage sludge compost 1.5g ⑤ 30g of contaminated soil + 9.0ml of methane production medium + raw waste C 1.5g + sewage sludge compost 1.5g_ This paper size is in accordance with Chinese National Standard (CNS) A4 specification (210X2W male) " 43 39498 (Jing first read the precautions on the back before filling out this page) Λ7 B7 43 86 2 1 V. Description of Invention (44) Implementation The test results of Example 4 are shown in Tables 7 and 8. (Please read the precautions on the back before filling this page.) Table 7 shows the concentration of tetraamethylene in the soil when purifying with pig iron scraps. Table 8 shows the aerial photo generated when the tetrachloroethylene in the soil was purified with pig iron scraps and the like. Table 7 Purification results of tetrahydroethylene in soil by raw dander (after 60 days of culture) PCE in soil (g / dry soil 1kg) pH ORP (mV) ①Contaminated soil (controlling sister) 23 6.63 307 ②Return to suspect + Compost 0 7. 58 -537 ③ Raw sickle A + compost 0 7.27 -375 ④ Raw suspect B + compost 16 7.25 -229 ⑤ Raw i 骟 C + compost 20 7. 27 -225 Staff Consumer Cooperative of Central Standards Bureau, Ministry of Economic Affairs The paper size for printing is applicable to the Chinese National Standard (CNS) A4 specification (210X297 mm) 44 3 94 98 4 3 B 6 2 1 A7 B7 V. Description of the invention Us) Production amount of gas during purification (after 60 days of culture) Ethylene and ethane conversion rate of PCE (⑹ Η2 (nl / kg- ±) CH4 {l / kg- ±) c〇2 (ml / kg-i) ① Contaminated soil (control group) 0 0 0 trace ②Returned iron + compost 79 3.4 trace 190 ③Pig iron scrap A + compost 73 2.3 〇243 ④Raw raw scrap B + compost 25 1.6 〇366 ⑤Raw scrap C + compost 7.6 1.8 〇414 Meanwhile, "tetrahydroethylene (PCE), pH, ORP in the soil" shown in Table 7 is the value after 60 days of culture. "Ethylene and ethane conversion rate of tetrachloroethylene (PCE)" shown in Table 8 is the ratio of tetrachloroethylene to ethylene and ethane within 60 days of culture. "H2, CH4, and Co2j represent the amount of pith produced per kg of dry soil in each period. Using the EBARA group and the pig iron chip A group, tetrachloroethylene in the soil can be purified to an undetectable level. At the same time, it can be seen that the use of raw discrimination chips is the same as that of Sugawara. Tetrahydroethylene can be dechlorinated and converted into ethylene and ethane. Especially when using raw cuttings A, that is, raw crumbs with small particle sizes, Tetrachloroethylene can be extremely effective in deaeration. When the slag is used to purify contaminated soil in the soil, the soil can be maintained at a neutral pH of 7.2 ~ 7.3 and the oxidation of the saturated atmosphere of silver is extremely difficult. Paper size selection Chinese National Standard (CNS) A4 specification (210X297 male f) 4 5 3 9 498 — — — — — — 01 —. 4 (Please read the notes on the back before filling this page) ^ 38621 Economy Printed by the Ministry of Standards and Labor ’s Consumer Cooperatives Ί 7 B7 V. Description of the invention (46) "Original environment" with original potential of -225 ~ 375nV. Therefore, compare the soil purification method using Liaoyuan iron and the soil using pig iron scraps In the purification method, the soil environment of the two is almost the same. The addition of ②③④ and ⑤ sister to the methane-generating extracting biological medium both generate carbon dioxide in the gas phase part of the kneading bottle, so there should be extractive growth. In other words, pig iron 1 is a substance that is not harmful to the growth of soil microorganisms. Pipe oil 俐 利 5 First prepare the same tetra-ethylene ethylene-contaminated soil as in SIS Example 4 or add another contaminated soil sample with different content of tetrachloroethylene. In this way, you can get 1 kg of dry soil and four gases in the soil. Ethylene contained 50 mg of contaminated soil, 75 mg of contaminated soil, and 140 mg of contaminated soil. Purification tests were performed on each contaminated soil. The experiment was the same as in Example 4, with a capacity of 125 m 1 Take 30 g of contaminated soil in a sample bottle scale, and then mix with 9.0 ml of the medium for methane generation in Table 6, 1.5 g of pig iron scrap A with a particle size of 500 wai or less, and 1.5 g of sewage sludge compost to measure the decomposition of tetrachloroethylene. The gas phase part of the sample bottle was replaced by nitrogen when the sample was prepared. The experiment was performed at room temperature and the pH in the soil was measured after 63 days. The oxidation potential of the saturated silver chloride electrode and the tetrachloroethylene were measured. Reduction Production of ethylene and ethane in Μ and gas phase. Actual test conditions ① Contaminated soil (5 S tetramethylene / kg dry refining soil) 30g (control group) ② Contaminated soil (50ag tetrahydroethylene / kg dry) Soil) 30S + methane generation (please read the notes on the back before filling this page) This paper size applies to Chinese National Standard (CNS) A4 (2 丨 0X297 mm) 46 3 9 4 9 8 Employees of the Central Standards Bureau of the Ministry of Economic Affairs Printed by the Consumer Cooperative 4 3 8 6 2 1 A7 B7 V. Description of the invention (47) Use 9.0ml of culture medium + 1.5g of raw soup shield A + 1.5s of sewage sludge compost ③ Contaminated soil (75ng tetrachloroethylene / kg dry soil ) 30g (control group) ④ Contaminated soil (75iag four atmosphere ethylene / ks dry-refined soil) 30s + methane generation medium 9.0m 丨 + raw interception MA 1.5g + sewage sludge compost 1.5g ⑤ contaminated soil (140 ng Four atmosphere ethylene / kg dry soil 干燥) 30g (control group) ⑥ Contaminated soil (140ms four gas ethylene / kg dry soil 炼) 30g + medium for methane generation 9.0 »1+ raw crumb A 1.5g + sewage sludge compost The test results of 1.5 g of Example 5 are shown in Table 9. From this table, it can be known that the soil containing 1kg of dry gas soil containing 1kg of dry gas contains 50bS, 75ns, and 140ns of high-concentration contaminated soil. It can be degassed with raw grains A and particle sizes of 500ϋΐ® or less. Ethane, showing the effectiveness of this soil purification method. In this soil purification experiment, the decomposition products of tetrachloroethylene were only produced in the gas phase and in the soil with the withdrawal of three gas ethylene and cis-DCE, and it was almost impossible to obtain chlorinated ethylene. In addition, pig iron scrap A is used to purify the soil contaminated with high concentration of tetrachloroethylene. The soil can be stably maintained at a neutral pH of 7.2 ~ 7.3, and the osmium oxide potential of the saturated gasified silver electrode is -350 ~. 3 80 i »V, The Original Environment. The "tetraamethylene, pH, 0RP in the soil" shown in Table 9 is the value after 63 days of culture. The "Ethylene, ethane conversion rate of tetrachloroethylene" shown in Table 9 is the ratio of tetrachloroethylene to ethylene and ethane after 63 days of culture. (Please read the precautions on the back before filling out this page) This paper size is applicable to Chinese National Standard (CNS) A4 (2! 0 X 297 mm) 3 9 49 8印 ι 印 $; 4386 2 1 at B7 V. Inventive reading (Aunt) Table 9 Purification results of suspected high-temperate four-atmosphere ethylene-contaminated soil (after 63 days of culture > PCE in soil (ag-PCE / kg- Conversion rate of ethylene and ethane in dry soil 1 PCE (%) pH 0RP (mV) ①Contaminated soil (control group) 45 0 6.71 360 ②Green cuttings A + compost 4.0 65 7.28 -380 ③Contaminated soil (control group) 73 0 6.75 345 ④Pig iron filings A + compost 19 58 7.19 -375 ⑤Contaminated soil (control group) 139 0 6.86 336 ⑤Pig iron filings A + compost 78 28 7.31 -347 (Read the precautions on the back before filling this page) This paper size is in accordance with Chinese National Standard (CNS) A4 specification (210 × 297 publicly available) 39498 43 86 2 1 at Β7 V. Description of the invention (49) It can be seen from the present invention that metal powders that are suspected of being powders or unbelievable powders are used in the present invention. It can be used for chlorinated organic compounds in a wide range of low to high concentrations of pollution. Achieve a high purification rate of substances. That is, the use of raw materials such as raw crumbs can be low-cost, safe and simple to process and purify pollutants contaminated by chlorinated compounds, and can effectively use industrial waste. Combined with a low-solubility soil improver, it is possible to prevent dissolved organic compounds from dissolving in the contaminated soil. At the same time, while maintaining the water retention capacity of the contaminated soil, purification can be achieved and the pollution of organic chlorine compounds that have been generated underground can be maintained. It will not penetrate deeper from the contaminated location to a deeper depth. Emu Oil? Li Fi Example 6 corresponds to the second aspect of the present invention. Practical Example 6 shows that even without adding anaerobic microorganisms from the former In the case of nutrition sources, halogenated organic compounds can also be decomposed by M. The appropriate principles for the use of tetrafluoride are: (1) metallic iron (comparative example), (2) manganese, (3) aluminum-silicon alloy, and (4) sodium hypophosphite. The standard electrode potentials of each reducing agent are pleased to be in Table 10. Table 10 The quasi-electron potentials of the suitable agents (please read the precautions on the back before filling out this page).檷 Quasi-electrode potential UV) (1) Jinguo-440 (2) Manganese-1180 (3) Aluminum-silicon alloy-1600 (4) Sodium hypophosphite-499 This paper is applicable to China National Standards (CNS) Α4 Specifications (2 丨 0 × 297 mm) 49 3 9 4 9 8 Λ7 4 3 86 2 1 __B7 V. Description of the invention (50) Will (1) gold drive 20g, (2) manganese 10g, ( 3) Aluminum-silicon alloy 1 and (Please read the precautions on the back before filling this page) (4) Add 20g of sodium hypophosphite to 6500g (water content of 60%) containing tetragas ethylene 1 5 0 »g / kg loamy soil, maintained at 200, and the subsequent state was measured. (2) and (3) The osmium oxide oxidation potential decreased to -500jiV or less within 1 hour, and it was maintained at -500bVM for the next 10 days. After 10 days, tetrachloroethylene can be completely dehalogenated to ethylene and ethane. (4) The oxidation potential decreased to -450mVM within 1 hour, and then held at -450n \ iM for 10 days. Four atmosphere ethylene was completely dehalogenated to ethylene and ethane after 10 days. In contrast, it took 5 days for the lutetium oxide potential of (1) to decrease to _400bV, and it remained at -400bV for the next 5 days. After 10 days, only 20% of tetrachloroethylene was dehalogenated to ethylene and ethane. Fen Fu Li 7 Comparison (1) The group containing only rhenium agent and no rhenium carbon source, and (2) the group containing the diagen agent and organic carbon source, where calcium-silicon alloy is used as the diagen agent (Pseudoelectrode potential-1900mV), organic tritium source uses sodium tritate. Printed in (1) and (2) of the Consumer Cooperatives of the Central Standards Bureau of the Ministry of Economic Affairs. Add 100g of calcium-silicon alloy to 65kg (55% moisture content) of clay soil with 200 m g / k g of trichloroethylene. In (2), add 70g of sodium acetate and other nutrition sources for 7s. Each group was maintained at a temperature of 2 and the subsequent state was measured. Both (1) and (2) decrease the oxidative peptogen potential to below 1 hour. (1) The redox potential was maintained at _500bVM for 10 days. After that, it gradually changed to an oxidized state. Between 40 days, the oxidation suitable potential was on the paper. The Chinese standard (CNS) A4 specification (210X 297) (Mm) 50 39498 43862 t A7 ______ 5. Description of the invention (Si) rose to OmV. Eighty percent of trichloroethylene is ethylene and ethane, and the remaining 20% is left in soil. In contrast, (2) maintain the osmium oxide potential within 40 days. At -500nVM, 99% of the three atmosphere ethylene can be ethylene and ethane. The kanji agent of the present invention is not easy to cover a stable oxide film on the surface, and is not easy to dissolve in water, so it is easy to contact with pollutants and improve decomposition speed. In addition, when B dyes are bottom-permeable materials such as clay soil or agglomerated silty soil, dehalogenation can also be carried out by adding a carbon source as the growth-removing substrate. (Please read the notes on the back before filling out this page) Printed and used by the Consumer Cooperatives of the Central Bureau of Standards of the Ministry of Economic Affairs (1) Gold powder (control group), (2) Sodium hypophosphite powder Ή or (3) 撺 Birch An aqueous solution of titanium acid is a kangen agent. The actual m condition is converted to dry soil with 120k g / kg of soil containing tetrachloroethylene. At the initial stage, the oxidation potential is + 350mV and the soil volume is 100b3. The results of the rounds (2), (3) reduced the entanglement potential to -450 nVK within 1 hour, and within 5 hours, the inner male maintained at -450b VM. Tetrachloroethylene is completely dehalogenated to ethylene and ethane after 5 days. In contrast, the 1 (1) group used a single knotting machine to mix the soil and metal completely within 10 days. After that, it would take 5 E 丨 to reduce the oxidative kangen potential to-400 m V. The next 5 days remained below -400 bV. Twenty percent of tetrachloroethylene is dehalogenated to ethylene and ethane after the 20th. Example 9 The ascorbic acid was used as the transport agent in each group. (1) Organic is not added to the group. The paper size is in accordance with Chinese National Standard (CNS) A4 (210X297 cm) 5 1 3949 8 A7 438621 B7 V. Description of the invention (52) Carbon source. In contrast, in the group (2), sodium gallate was used as the organic carbon source. (Please read the precautions on the back before filling out this page.) Use the converted dry soil as a clay containing tetrahydroethylene lOOng / ks. The initial oxidation potential is + 32〇1 ^. 11 is 6.5. Results of the W-channel (1) and (2) groups were all reduced to +130 mVM within 1 hour after the entanglement agent was injected. (1) During the 10th day, the oxidative potential was maintained at + 130bVM, after which the photoperiod changed to an oxidized state. After 40 days, the oxidative potential was gradually increased to +3 00 »^.卩 11 gradually decreased from 6.3 on the 0th to 5.5 on the 40th. Siqi ethylene was 50% converted into ethylene and ethane, and the remaining 50% was left in the soil. In contrast, (2) the oxidative tunogen potential gradually decreased after that, to -150mVM after 20 days, and to -150nVM after 40 days. The pH gradually decreased from 7.5 on day 0 to 6.8 after 40 days. 99.9% of tetrachloroethylene is ethylene and ethane. The raw cocoon used in this actual pickled state is water-soluble, so pollutants contaminated with organic compounds can be contacted with kanogen agents to promote kangaric de-salinization reactions. Printed by the Consumer Standards Cooperative of the Central Bureau of Standards of the Ministry of Commerce " The original agent used in this experimental state has a potential of approximately equal to or below the potential of the quasi-electrode potential. Therefore, it has a large potential difference from the halogenated organic compound. , Which can accelerate the advantages of dehalogenation. In addition, when the pollutants are low-permeability materials such as clay soil and agglomerated silty soil, they can also be dehalogenated in conjunction with the organic carbon source of microbial growth substrate. At the same time, these rhenium agents do not appear to be passivated. Window example 1 〇 This paper size applies Chinese national standard (〇 «) / \ 4 specifications (210: > < 297 public 1) 52 39 498 43 86 2 1 A7 __B7 V. Description of the invention (5 3) The invention It has been shown that halogenated aromatic compounds can be decomposed. 20g of gold-layer iron was added to 6s loam soil with a concentration of 110g / ks of PCP. In the group 10-1, another 1 liter of the nitric acid-cancerous culture medium shown in Table 11 was added. In contrast, the 10-2 group is the control group, and only 1 liter of water is added. Table 11 Addition amount of nitric acid-producing olive organism medium potassium 4.5g / 1 potassium 8.5g / 1 sodium bicarbonate 5.0g / 1 hexahydrate and atmospheric magnesium 0.2g / 1 yeast extract 0.1 g / 1 Dilution water tap water pH 6.9 ~ 7.4 (please read the precautions on the back before filling this page). Ding-5 The Bank of China's Ministry of Finance will print $ in the negative quasi-government consumer cooperative, and then, after mixing Maintained at 281C, and then measured the changes in PCP concentration and product concentration. The results are shown in Tables 12 and 13. This paper size applies Chinese storehouse standard ([-! ^) 8 4 specifications (210 乂 297 mm) 3 9 4 9 8 43 86 2 1 at B7 V. Description of invention (54) Table 12: 10-1 Result Compound name: after 20 days and 40 days? C? (Mg / kg) 10.1 0.58 0. 0 1 ^ TeCPiffig / kg) 0.00 2. 0 0.00 CP (η g / kg) 0.00 2.3 0.02 Phenol 0.00 1.2 3.1 Eh ( aV) + 312 -380 -423 Table 13: Results of the 10-2 group Compound name PCP (丨 g / kg) after 20 days and 40 days after 10.2 2.4 0.9. TeCPfmg / kg) 0.00 1.0 0.00 CP (ig / kg) 0.00 2.1 2.8 Phenol 0.00 0.8 1.0 Eh (aV) + 308 -1 70 + 118 Printed by the Women's Workers Consumer Cooperatives of the Ministry of Economic Affairs, Zhongrui Standard Bureau ^ (Please read the precautions on the back before filling this page) -〇, Table 12 and In Table 13, TeCP and CP each represent 2,3, 5,6-tetraphenol and 3-phenol. At the same time, Eh is a value converted to a standard electric hibiscus potential for a standard hydrogen electric hibiscus. 0 Comparative Example 10-1 and Group 10-2 show that pentaphenol can be rapidly decomposed. This paper size applies to the Chinese National Standard (CNS) Λ4 specification (210X 297 mm) 54 3 9498 438621 B7 Employees of the Intermediate Standards Bureau of the Ministry of Economic Affairs, China Consumers' Union, Yinfan 5. Inventive Notes (55) 1 1 10 -1 Pentachlorophenol in the group should be decomposed into tritium through 2,3,5,6-tetrachlorophenol and / or 3-chlorophenol ί 1 I simultaneously 2, 3, 5, 6-tetrachlorophenol and 3-chlorophenol m This can be further divided into 1! I is decomposed into other compounds 0 1 | Please II directly JL1 read 1 I read 1 | Real W Example 1 1 mainly corresponds to the third aspect of the present invention. The back of 1 I Example 1 1 uses the oxidation state nitrogen of Table 1 4 in the original state of the use of biological culture medium and Table 15 for the formation of microorganisms for the formation of formazan microorganisms (control group) to purify the four atmosphere of the second hospital item 1 fill Λ contaminated soil 〇 Table 14 The content of the oxidized nitrogen in the medium composition of Table 4 corresponds to 23% by weight of the organic carbon page W 1 〇 Purification experiments are performed at room temperature (12 ~ 23C > 30 days 1 test 1 i 1 determine the properties of the soil The changes are recorded in Table 16. The measurement of pH 01 is adjusted to soil pure water = 1: 1 (wt), and then measured by Toya Denki 1-wave industrial pH meter HH-5 B type. For saturated silver chloride electrode Measurement of oxidative suitability iT I in situ (0RP) to prepare the soil: anaerobic water = = 1 1 (wt), 1 I Immerse the electrode of UK-2020, a central scientifically manufactured meter, UK-20 3 0, and leave it for 30 minutes Measurement 1 I 〇 Further, the pair of saturated gasified silver electrodes shown in this example Oxidation of the original source r1) Potential »Metal electric hibiscus for platinum electrode 9 Use saturated silver chloride as the ratio [yJ I The position shown on the pole is determined. The analysis of soil atmospheric vinyl is based on 1 1 Method developed by Yokohama National University (Miyamoto Ken--etc., "A method for determining the content of halogenated organic compounds in the soil with low boiling point 1 1 point J Journal of the Water Environment Society» 1 1 1995 Vol. 8 * No. 6 9 477 ~ 488 Page), after extraction with acetic acid, 1 I was converted to Guiyuan and M Yue Li gas chromatography G-5000. F ID detector, 1 | 20% TCP ch Γ 0 IQ 0 SO rb WAV DHCS 60 -80 aesh column analysis 0% hydrogen produced in gas I 1 i phase carbon dioxide > methane nitrogen gas determination 1 then 1 1 GL scientific gas phase analyzer GC-3 20 TCD detector, A ctive 1 1 Paper size applies Chinese National Standard (rNS) A4 specification (210X297 mm) 55 3 9 498 4 3 8 6 2 1 Λ7 Β7 V. Description of invention (56) carbon 30/60 or Mol ecular sieve 13X. The acidic nitrogen and nitrite nitrogen ions in the soil were measured by Hitachi Anion Chromatograph 2010i. Soil: pure water = 1: l (wt) adjusted extraction water. Table 14 Bioreduction medium for oxidation reduction of nitrogen (please read the precautions on the back before filling in this page) Ingredients potassium nitrate 4.5 g / 1 potassium acetate 8. 5 g / 1 sodium bicarbonate 5.0 g / 1 Water and magnesium chloride 0.2g / 1 Yeast extract 0.1 g / 1 Diluted water tap water pH 6, 9 ~ 7.4 Printed by the Consumer Cooperatives of the Central Standards Bureau of the Ministry of Economic Affairs Table 15 Addition amount of methanogenic microorganism culture medium L-cysteine Amino acid 塩 塩 塩 0. 1 g / 1 Polyprotein Chen 2 · 0 g / 1 Glucose 2 * 5 g / 1 Sodium acid 2.5 g / 1 Methanol 5. 0 m 1/1 Sodium bicarbonate 5.0 g / 1 Nine water and Sodium sulfide 0.1 g / 1 Yeast extract 1.0 g / 1 Diluted water tap water pH 6. 9 ~ 7. 2 This paper size applies Chinese National Standard (CNS) A4 specification (2 丨 0X2? 7 mm) 56 3949 8 43 86 2 1 Member of the Bureau of Standards of the Ministry of Economic Affairs of the People's Republic of China, J-F, Cooperative Association, A7, B7 V. Description of the invention (57) 1 1 Purification η Four gas and η contaminated soil (Dye! | Concentration about 2 5 ntkg dry Suspected soil) η Tuobao test to search Sample of Guang M I 1 I bottle weigher takes 30g of contaminated upper soil and then lowers the mixture of cattle under VX to train 1 1 | Basic > Determination of white tetrachloroethylene decomposed soil after 30 days Property A. Read 1 1! Change status, etc. (Table. 16). Gold powder is reduced to m powder using Wako Pure M grade 1 back 1¾ of Γ. At the same time, when steel samples are used, M helium replaces the sample bottle. The gas department 5. Italian food 〇 Ύ item and then 1 4 S. 旃 conditions this page 1 ① contaminated soil 30 ε _ < · 1 I ② contaminated soil 30 Ε + water S .0〇] + m 07 g 1 1 ③ 30 g of contaminated soil + 90ml of biological removal medium for oxidized nitrogen through the original-! 1 1 Order 0. 07 S 1 ④ 30 δ of contaminated soil ♦ Medium for methanogenic microorganisms 9. 0 B1 1 +原 锇 i 1 0. 07 g The experimental results of II are shown in Table 16. It can be determined that t can be used in the oxidation state nitrogen m original r \ culture medium 9 not only tetragas ethylene can be dechlorinated to form ethylene and ethylene 1 and j can inhibit the blackening of methane and methane production> The occurrence of sulfur odor and odor can be found at the same time III. The nitrogen produced can be diluted by the hydrogen produced. In addition, no residual oxidized nitrogen and sub-oxidized nitrogen in the soil 1 i have been found. 0 1 1 In the group of adding metal and water, ρ Η is greatly reduced, and the oxidative passivated potential of saturated I 1 and oxidized silver electrodes also rises to + 2 mV after 30 days.> Because 1 1 cannot fully degassing Kanbara Decomposition 0 so the results are-part of tetrachloroethylene 1 1 ene is still left in the soil. The conversion of ethylene is only 26% 〇 This shows »1 1 | The group with only metal powder is difficult to maintain in the long term Current state of restoration * Only 1 1 paper size applies to China Standard home U, NS) Λ4 current cell (210X2W mm) 57 3 9 4 9 8 f 438621 A7 B7 V. invention is described in (58)

解 分 地 定 安 Jl·11 碧 可10 才近 始幾 , 生 在產 存 會 時組 同 之 應末 反粉 物屬 生金 使加 劑添 養只 營. 加外 添此 有 C 氣 氫 之 % 堪 生 氮撤 態成 化生 氧烷 加甲 添加 為添 因 » , 氣 地氮 對的 相生 ο 0 性中 險組 危之 之基 炸養 爆培 有物 想生 推微 此用 因原 安臭 高有 有現 示發 顯 , 中 氣 組 氫基 釋養 稀培 Μ 物 可生 , 微 碳成 化生 氧烷 二甲 〇 的加色 生添變 產在壤 中有土 基只及 養 。生 培性產 物全氣 —— —— —— ——ο— — > —(請先閱讀背面之注意事項再填寫本頁) 丁 '-b 經1¾—部中决標車局MJ-消费合作社印掣 本紙張尺度適用中國國家標準(CMS ) Μ規格(210X 297公釐) 58 3 9 498 438621 Λ7 B7 經濟部中央標準局員工消費合作社印製 五 '發明説明(5$ 表16 土壤中四氛乙烯(PCE)之淨化结果(培養30日後) ①污染土壤 ②污染土壤 ③污染土壤 Φ污染土壤 +水 +氧化態 +甲烷生 (控制組) +金臛戡 氮還原培 成培着基 養基 +金屬嫌 +金羼嫌 土壤中PCE 22.5 8.6 0.0 'J 0.0 (ag-PCE/ kg) pH 6.82 5.37 7.48 7.52 ORP(mV) +289 *2 -376 -542 PCE之乙烯乙烷 0 26 81 84 轉換率(%) H2(inl/kg_ 土) 0.00 1.3 2.8 3.5 CH4 (苗1/ kg 土) 0.00 0.07 0.00 0.52 C〇2 (al/kg土) 0.00 0.15 0.10 182 N2(Bl!;/lcg 士) 0.05 0.04 110 0.10 N〇3-HUl/kg±) 0.5 0.3 0.0 0.0 N〇2-N(Bl/kE:± ) 0.0 0.0 0.0 0.0 臭氣 無 無 無 有 變色 無 一部份變色 變色成 變色成 成淡藍色 淡藍色 黑攥色 本纸張尺細中 59 39498 I——ί—ίο—— ♦- (請先閲讀背面之注意事項再填寫本頁) T* -" 438621 A7 經Μ部中决標準局員工消费合作社印製 __B7五、發明説明(6〇 ) 本發明之第3態樣中,由於使用之營養源中含有機態 碳之20〜50重量%氧化態氮,因此在分解鹵化有機化合物 之際,可以抑制土壊之黑變、及產生甲烷氣體、确醇等惡 臭氣體。 管)fe例1 2 實施例12中,以水溶性有機碳源供給有機態碳。 對5kg之含10bs有機氣化合物/ kg 土壤(水份60%), 各添加6g之(1)葡萄耱、(2)糖蜜廢液、(3>堆脃為有機碳 源,再添加20〇ag之曾養塩類,維持於28X:溫度下。 再測定其後的狀態。 (1)及(2)中,厭氣性细菌數在數日中增殖至107生菌 /g 土,對飽和氛化銀電極之氧化堪原電位(0RP)則在 30日中維持在- 600bV以下,因此四氯乙烯可Μ脫鹵化成乙 嫌、乙烧。 相對地,(3)中微生物增殖至107生菌/ g 土時須時 2 0日,0 R P在1 3日Μ後開始上昇,3 0日後為-2 3 m V。四氯乙 烯則有50%KCDCE(顒-二氢乙烯)之狀態餘留,因此無法 充份脫鹵化。 奮撫例13 對200kg之含30mg_化有機化合物/ kg 土壤(水份 65%)添加240g之葡萄糖為有機碳源,再添加8g之其他曾 養塩類,冬季之淨化作業則各ΚΠ)覆以聚乙烯膠布溫室, 並Μ溫水加潙(平均溫度2 2 1C )、( 2 )好外放置之條件處理 操作。 (請先閱讀背面之注意事項再填寫本頁) 本紙張尺度適用中國國家標4Μ CNS ) Λ4規格(2ΙΟΧ 297公釐) 60 39498 43 86 2 1 Αν B7五、發明説明() 在(1)中,厭氣性细菌數在數日内增殖至107生菌/ g 土, ORP在30日中維持於-600nVM下,因此四氯乙烯可 烷 乙 、0 乙 成 化 齒 晚% 地 對 相 ε 有留 /烯餘 菌乙態 土 在 在 時 , 須高 物昇 生始 微開 , 後 中 曰 生氯 7 } ο 四 1 至VO ra 殖 2 f 5 增 + 可 才 0 留化 餘 鹵 解脫 分份 法充 無法 %無 M % 為 / 後順 日E( 狀 烯 乙 氯 的 Β 物 烯 染 乙 污 氯 之 四 染 之 。Β内 樣物 坑 態化 泥 4 0 水 第有 於 之化 放 明鹵 儲 發因 取 本在 据 應程 内 對工 地 要化 。廠 主淨化廠 14壤淨工 例 土行學 施染進化 實 汚置自 位 原 約 度 m 染 污 均 平 壤 土 染 作 操 化 淨 施 實 壤 土 作 操 法 方 種 3 述 下Μ 嫌 步 化 淨 本 法 方 (讀先閱讀背面之注意事項再填寫本頁) ο. 經濟部中戎標準局員_τ消费合作社印袈 2 表 前及 加基 添養 在培 , 物 次生 其微 〇 用 内原 器堪 容氮 性態 5η水化 將漏氧 可不之 機之14 鏟桶表 倒製將 用板 . 使鋼時 3Β時 10小 積 膻 入 移 埔 土 染0 內 坑 泥 水 之 3 之 5 液機 溶鏟 液倒 養用 營使 Α)再 劑 , 養內 營桶 為製 稱板 下鋼 Μ入 /IV 基加 — 添 養 } 培% 用01 物 4 生之 微壤 成土 生 3 院2η 甲0. 4 之 壤 土 /|\ 3 m 之 % 營 輿 壤 土 拌 混 機 鏟 倒 Μ-ΓΤ ο 使 將再 次 , 再内 0 桶 拌製 混板 Α 網 劑入 養加 營添 與 A 壤劑 土養 將營 再 後 之 中 桶 板 ο _____ A 篇 劑入 養加 將 次 之 壊 土 營 與 壤 土 拌 混 再 〇 A 4 劑 1.養 添 A 0 驀 營 養 曾 與 壤 土 將 本紙張尺度適用中國國家標潭(<:邮以4規格(210:〇97公釐} 11 6 3 9 498 4386 2 1 B7 Μ碲部屮"標準局負J消費合作社印$1 五、發明説明(62) 1 | m A 充 份 混 拌 後 > 將 堪 原锇 撤 佈 m 板 製 桶中之土 壤內,再 1 I 一 次 混 拌 〇 將 混 拌 之 土 壤倒 回 水 泥 坑 内 〇 1 1 I [方法2 ] 1 I 讀 | 將 5 α 3之水泥坑內汚染土壤Μ倒鏟櫬移入前述鋼板製 先 閱 1 I 讀 1 桶 内 〇 其 次 將 1 . 1 1D 3 (土壤 之 22 V 0 1 % )之前述營養劑A 背 面 (' 之 1 I 添 加 於 m 板 製 桶 内 再 使用 倒 鏟 櫬 混 拌 土壤與營 養劑A。 注 意 η | 1 1 事 1 充 份 混 拌 土 壤 與 營 養 劑 A後 » 將 遢 原 m 撖佈於鋼 板製桶中 項 再 1 之 污 染 土 壤 内 9 再 一 次 混拌 〇 混 拌 後 之 土壤再倒 回水泥坑 本 W 頁 1 内 0 1 | [方法3] 1 1 1 將 5 9 3之水泥坑內污染土壤Κ倒鏟機移入前述網板製 1 訂 1 桶 内 〇 其 次 > 於 添 加 前 1 5〜 20小 時 9 將 表14之氧 化態氮堪 原 用 微 生 物 培 養 基 及 表 15之 甲 烧 生 成 微 生物用培 養基,及 1 1 懸 浮 有 埵 原 嫌 之 m 浮 液 (以下稱之營養劑B)0.2n3 (土壤之 1 i 4 V 0 196 )添 加 入 m 板 製 桶, 再 使 用 倒 鏟 櫬混拌土 壤及營養 劑 B〇 之後再將0 .2 m 3 (土壤之4 V 〇\96 )之營養劑B 添加人 Λ 1 1 m 板 製 捅 内 » 使 用 倒 鏟 機混 拌 土 壤 及 營 養削B。再次將 1 ! 0 . 7m 3 (土 壤 之 14 V 0 1 % )之曾養劑B 添加入網板製桶内, 1 1 將 其 充 份 混 拌 0 混 拌 後 之土 壤 再 倒 回 水 泥坑内。 1 1 將 方 法 1〜3 混拌之土壤- -部份取出後經10m m網目篩 1 1 網 過 篩 ί Κ 巨 視 確 定 混 拌後 土 壤 内 土 壤 塊之量, 结果顯示 I I t 方 法 1 及 方 法 3 之 土 壤内 土 壤 塊 為 土 壤量1〜10% ,相 1 I 對 地 方 法 2 中 土 壤 為 1 5 〜30% » 因 棍 拌程度會 因營養劑 1 1 1 之 添 加 方 法 及 混 拌 方 法 而異 0 1 1 本紙張尺度適用中國國家標率(CNS ) Λ4規格(210X29?公釐) 62 3 9 498 B7 五、發明説明(6 3 ) 但不論方法1〜3,為防止混拌後外部氧氣之出入,水 泥坑内土壤之表面均覆蓋聚氯乙烯膠布而Μ鐵板固定。此 外,除以聚氣乙烯膠布覆蓋之方法Μ外,亦可ΜΚ水覆蓋 至土壊表面5〜15cm程度將土壤浸水,Μ抑制外部氧氣之 出入並保持土壤内充足之水份。 同時,方法1〜3中均將土壤再移回水泥坑内,此乃 是為防止四氣乙烯等流出。在實際中,將地中之污染土壤 移入桶内,再於桶内混拌污染土壤及營養液,其次再將混 拌物移回原先移出污染土壤之坑內即可。亦或不在桶内混 拌,而在現場之地中混拌亦可。 土壤中之四氯乙烯濃度在聚氛乙烯膠布覆蓋後經2個 月後測定。此結果示於表17。 表17 四氛乙烯污染土壤淨化工程之结果 曰 數 方法1 方法2 方法3 第0日之P C Ε濃度(m g / 1 ) 5 5 5 2個月後之PCE濃度Ug/ 1) 0.01 0.55 1,9 分解率 99.8 89 62 經濟部中央標隼局負工消費合作社印製 (請先閱讀背面之注意事項再填寫本頁) Μ方法1混拌之土壤有99.8%被分解、而方法2中有 89%、方法3中則有62%分解。因此可知,以如方法1, 將營養劑分數次添加、混拌之場合.可以提高其分解率。 此外,亦可知入如方法2,將營着液與土壤混拌後,再添 加粉末彤態之缠原劑之場合,亦可提高分解率。 本紙張尺度適用中國國家標準(CNS ) Α4規格(210Χ297公釐) 63 3 9 49 8Ding'an Ding'an Jl · 11 Beck 10 is only near the beginning, born at the time of the production meeting, the same anti-powder material is gold, so that the additives are nourished. In addition to this, there is a percentage of C gas hydrogen Kansas nitrogen withdraws into biochemical oxane plus formazan added as an additional factor », the interphase of gas-ground nitrogen pairs ο 0 The base of the middle-risk group of the risk of frying and cultivating something that wants to be promoted to promote this use is because the original odor is high It has been shown that hydrogen-based release nutrients from the gas group can be grown, and the addition of microcarbons to the oxygenated oxane dimethyl oxine can produce soil-based nutrients in the soil. Biochemical products full gas —— —— —— ο— — > — (Please read the precautions on the back before filling out this page) Ding'-b Jing 1¾—Ministry of China Final Vehicle Bureau MJ-Consumer Cooperative The size of the printed paper is in accordance with the Chinese National Standard (CMS) M specification (210X 297 mm) 58 3 9 498 438621 Λ7 B7 Printed by the Consumers 'Cooperative of the Central Standards Bureau of the Ministry of Economic Affairs of the People's Republic of China to print the 5' invention description (5 $ Table 16 Four atmospheres in the soil Purification results of ethylene (PCE) (after 30 days of cultivation) ① Polluted soil ② Polluted soil ③ Polluted soil Φ Polluted soil + Water + Oxidation state + Methanogenesis (control group) + Gold sulphur nitrogen reduced to cultivate base + metal + PCE 22.5 8.6 0.0 'J 0.0 (ag-PCE / kg) pH 6.82 5.37 7.48 7.52 ORP (mV) +289 * 2 -376 -542 PCE ethylene ethane 0 26 81 84 Conversion rate (% ) H2 (inl / kg_ soil) 0.00 1.3 2.8 3.5 CH4 (seed 1 / kg soil) 0.00 0.07 0.00 0.52 C〇2 (al / kg soil) 0.00 0.15 0.10 182 N2 (Bl!; / Lcg) 0.05 0.04 110 0.10 No.3-HUl / kg ±) 0.5 0.3 0.0 0.0 No.2-N (Bl / kE: ±) 0.0 0.0 0.0 0.0 Odor No No No Discoloration No part of discoloration Discoloration becomes discoloration into light blue light blue black black This paper ruler is thin 59 39498 I——ί—ίο—— ♦-(Please (Please read the notes on the back before filling in this page) T *-" 438621 A7 Printed by the Consumer Consumption Cooperative of the Bureau of Standards of the Ministry of M__B7 V. Description of the invention (60) In the third aspect of the present invention, The nutrient source used contains 20 to 50% by weight of oxidized nitrogen in organic carbon. Therefore, when the halogenated organic compounds are decomposed, the blackening of soil can be suppressed, and malodorous gases such as methane gas and alcohol can be generated. Tube Example 1 2 In Example 12, organic carbon was supplied from a water-soluble organic carbon source. For 5kg of 10bs of organic gas compounds per kg of soil (60% moisture), add 6g each of (1) grape mash, (2) molasses waste liquid, (3 > heap 脃 as an organic carbon source, and then add 20〇ag The once-raised tadpoles were maintained at 28X: temperature. The subsequent state was measured. In (1) and (2), the number of anaerobic bacteria proliferated to 107 bacterial / g soil in a few days, and saturated atmosphere The oxidation potential (0RP) of the silver electrode was maintained below -600bV for 30 days, so tetrachloroethylene could be dehalogenated to Ethylbenzene and Ethylpyrene. In contrast, the microorganisms in (3) multiplied to 107 bacteria / It takes 20 days for g soil, 0 RP starts to rise after 13 days, and after 30 days it is -2 3 m V. Tetrachloroethylene has 50% KCDCE (fluorene-dihydroethylene) remaining, Therefore, it cannot be fully dehalogenated. Fenfu Example 13 Adds 240g of glucose as an organic carbon source to 200kg of 30mg_ of organic compounds per kg of soil (65% moisture), and then adds 8g of other previously cultivated pupae for purification in winter. Each operation is covered with a polyethylene blanket greenhouse, and heated with warm water (average temperature 2 2 1C), and (2) treated under good conditions. (Please read the precautions on the back before filling in this page) The paper size is applicable to Chinese national standard 4M CNS) Λ4 specification (2ΙΟχ 297mm) 60 39498 43 86 2 1 Αν B7 V. Description of the invention () In (1) The number of anaerobic bacteria proliferated to 107 bacterial / g soil within a few days, and ORP was maintained at -600 nVM for 30 days, so tetrachloroethylene alkane and 0 ethanoate were left late for phase ε. In the presence of ethylenic bacteria, the soil should be slightly opened after the ascension, and then generate chlorine 7} ο 4 1 to VO ra colony 2 f 5 increase + can be 0 Can not be% without M% is / after the day E (like the ethylenic chloride B substance olefin dyeing ethyl pollution chlorine four dyeing. B internal sample pit state sludge 4 0 water first to put the bright halogen storage storage Due to the cost, the construction site should be chemically processed. The plant owner ’s purification plant has 14 soil cleanliness, soil engineering, evolution, actual pollution, and the original degree of m. Method 3 of the operation method is described below. Please fill in this page again) ο. Member of Zhongrong Standards Bureau, Ministry of Economic Affairs_τ Consumer Cooperative Co., Ltd. 2 The table and the supplementary supplements are cultivated in the culture, and the products are inferior. The internal proton can accommodate nitrogen behavior 5η Hydration will leak Oxygen's No. 14 shovel bucket table will be used to make the plate. Make the steel 3B, 10 small accumulations into the soil and dye 0 in the pit mud, 3 of the 5 water in the machine to dissolve the spatula and use it to raise the water. The agent for raising internal camps is the steel plate under the plate / IV base plus-supplementation} cultivation% using 01 things 4 micro soil to form soil 3 3 2 2 A 0.4 soil / / \ 3 m% Yingyu loam soil mixer shoveled down Μ-ΓΤ ο so that it will be mixed again, and then inside 0 barrels to mix the mixed plate A net agent to raise and add camp and A loam agent soil to raise the camp to the middle of the barrel board _____ A articles Add the agent into the soil and mix the second soil camp with the loam again. 0 A 4 Agent 1. Nourish and add A 0. The nutrition has been used with the loam soil to apply the Chinese paper standard (&post; 4 specifications (210: 〇97mm} 11 6 3 9 498 4386 2 1 B7 Μ Tellurium " Standard Bureau Negative J Consumer Cooperative Co., Ltd. $ 1 5. Description of Invention (62) 1 | m A After thorough mixing > Dismantle the original soil in the m-plate bucket, and mix again with 1 I. Pour the mixed soil back into the cement pit. 0 1 1 I [ Method 2] 1 I read | Move the contaminated soil in the cement pit of 5 α 3 into the aforementioned steel plate. Read 1 I read 1 bucket. Secondly, 1.1 1D 3 (22 V 0 1% of soil). The back of the aforementioned nutrient A ('-1 I was added to the m-plate bucket, and then the soil and nutrient A were mixed with a backhoe. Note η | 1 1 Things 1 After thoroughly mixing the soil and nutrient A »Put the 遢 原 m 撖 in the contaminated soil of the steel plate bucket 1 and 9 again and mix again. 0 The mixed soil is poured back Cement pit book W Page 1 inside 0 1 | [Method 3] 1 1 1 Move the contaminated soil in the cement pit of 5 9 3 K backhoe to the above-mentioned stencil board 1 order 1 bucket 0 second> before adding 1 5 ~ 20 hours 9 The oxidized nitrogen-containing microbial culture medium in Table 14 and the microbial culture medium in Table 15 were used to generate microorganisms, and 1 1 Suspension solution of Sugawara (hereinafter referred to as nutrient B) 0.2n3 ( 1 i 4 V 0 196 of soil) was added to the m-plate bucket, and then the soil and nutrient B were mixed with a backhoe and then 0.2 m 3 (4 V of the soil 0 96) of nutrient B Added by Λ 1 1 m inside the slab »Use a backhoe to mix the soil and nutrient shaving B. Add 1! 0.7m 3 (14 V 0.01% of soil soil) of former nutrient B into the stencil drum, 1 1 Mix it thoroughly 0 Mix the soil soil and pour it back into the water puddle. 1 1 Method 1 ~ 3 mixed soil--Partially removed and sieved through a 10mm mesh screen 1 1 The mesh was sieved Κ Jushi determines the amount of soil mass in the soil after mixing, the results show II t Method 1 and Method 3 The amount of soil in the soil is 1 ~ 10% of the soil, phase 1 I is on the ground. Method 2 is 1 ~ 30% of the soil. »The degree of stick mixing will vary depending on the addition method and mixing method of the nutrient 1 1 1 0 1 1 This paper size applies Chinese National Standards (CNS) Λ4 specifications (210X29? Mm) 62 3 9 498 B7 V. Description of the invention (6 3) However, regardless of methods 1 ~ 3, in order to prevent outside oxygen from entering and mixing after mixing The surface of the soil in the cement pit is covered with PVC tape and the M iron plate is fixed. In addition, in addition to the method M covered with polyethylene gas blanket, the water can be covered with KM water to about 5 ~ 15cm on the surface of the soil, so as to soak the soil, and M can prevent the ingress of external oxygen and maintain sufficient water in the soil. At the same time, in methods 1 to 3, the soil is moved back to the cement pit, which is to prevent the outflow of ethylene and other gases. In practice, move the contaminated soil in the ground into a bucket, mix the contaminated soil and nutrient solution in the bucket, and then return the mixture to the pit that was originally removed from the contaminated soil. Or do not mix in the barrel, but in the field. The concentration of tetrachloroethylene in the soil was measured 2 months after the vinyl blanket was covered. This result is shown in Table 17. Table 17 Results of the purification project of soil with four atmospheres of ethylene pollution Method 1 Method 2 Method 3 PC E concentration at day 0 (mg / 1) 5 5 5 PCE concentration after 2 months Ug / 1) 0.01 0.55 1,9 Decomposition rate 99.8 89 62 Printed by the Consumers' Cooperative of the Central Bureau of Standards of the Ministry of Economic Affairs (please read the precautions on the back before filling this page) Μ99.8% of the mixed soil is decomposed and 89% in the method 2 In Method 3, 62% were decomposed. Therefore, it can be known that when the nutrient is added and mixed in several times as in Method 1, the decomposition rate can be improved. In addition, it can also be seen that if Method 2 is used, the solution is mixed with the soil, and then the powdered entanglement agent is added to increase the decomposition rate. This paper size is applicable to China National Standard (CNS) A4 specification (210 × 297 mm) 63 3 9 49 8

Claims (1)

經濟部中央標準局員工消費合作社印製 A84386 2 1 ?88 D8六、申請專利範圍 1. 一種淨化因鹵化有機化合物污染污染物之方法,該方 法具有添加25¾下對標準氫電極之標準電槿電位為 130biV〜2400bV之還原劑及從属營養型厭氣性微生物之 營養源的步驟,其中前述堪原劑為适原鐵、生鐵、嫌 —矽合金、钛合金、鋅合金、錳合金、鋁合金、鎂合 金、鈣合金及水溶性化合物之群體中選擇的至少1種 〇 2. 如申請專利範鼷第1項之方法,其中前述邐原劑為25 t下對摞準氫電極之標準電極電位為-400®V〜-2400nV ,係由理原級、生鐡、鐵一矽合金、鈦合金、鋅合金 、錳合金、鋁合金、鎂合金及鈣合金中選擇的至少1 種者。 3. 如申讅専利範圃第1項之方法,其中前述1原劑為含 适原截者。 4. 如申請專利範圍第1項之方法,其中前述埋原銷為含生雜W。 5. 如申請専利範圃第1項之方法,其中前述瑁原劑為由 鐵一矽合金、钛一矽合金、钛一鋁合金、鋅—鋁合金 、猛一续合金、銘一鲜—耗合金、銘一錫合金、銘一 矽合金、鎂-錳合金、及鈣一矽合金之群體中選擇的 至少1種者。 6. 如申請専利範圍第1項之方法,其中前述遢原劑為水 溶性化合物者。 7. 如申諳專利範園第6項之方法,其中前逑®原劑為有 (請先鬩讀背面之注意事項再填寫本頁) 本紙張尺度適用中國國家樣準(CNS ) A4規格(210 X 297公釐) 64 3 9 49 8 ABCD 4386 21 六、申請專利乾圍 機酸或其衍生物、次磷酸或其衍生物、或碕化物之塩 者。 (請先閱讀背面之注意事項再填寫本頁) 8. 如申請専利範匾第1項之方法,其中前述遢原劑為具 有粒徑500# b以下之粉末者。 9. 如申謫専利範_第1項之方法,其中前述污染物之含 水率至少為25重量%者。 10. 如申謫專利範園第1項之方法,其前述添加步驟之後, 另有保持前述污染物於PH4.5〜9.0範圍之步驟,以促 進前述鹵化有櫬化合物之遢原性脫鹵化者。 11. 如申請專利範園第1項之方法,其中前述添加步驟後, 另有保持前述污染物在PH4.5〜9.0範園及理原環境之 步驟者。 12. 如申請専利範園第1項之方法,具有在前述污梁物中 添加有櫬質系各種堆肥、堆肥化有機物,或含有機物 之廢水及醆棄物,再將之混合之步驟者。 13. —種因鹵化有機化合物污染的污染物之淨化方法,該 方法具有將25C下對標準氫轚極之檷準電位13〇1^〜 經濟部中央標準局員工消費合作社印策 -2 4 0 0 m V之适原劑添加於前述污染物中之步驟,其前述 堪原瘌為由《原鐵、生嫌、戡一矽合金、钛合金、鋅 合金、錳合金、鋁合金、鎂合金、鈣合金及水溶性化 合物之群艚中埋擇的1棰Μ上。 14. 如申請專利範圍第13項之方法,其中前述遢原劑在 25t:下對棵準氫罨極之檁準電極電位為- 400bV〜 -2400HV,且為由逐原鐵、生截、锇一矽合金、钛合金 本紙張尺度適用中國國家榇準(CNS ) A4規格(210 X 297公釐) 65 3 9 4 9 8 438621 經 濟 部 央 標 準 局 員 工 消 合 作 印 製 D〇 穴、申請專利範圍 1 I 鋅 合 金 、 錳 合 金 、鋁 合 金 、 鎂 合 金 % 及 鋁 合 金 中 m 1 1 1 擇 的 至 少 1 種 者 1 1 1 1 5 .如 申 請 專 利 梅 園 第 13項 之 方 法 9 其 中 刖 述 堪 原 劑 為 含 ^~、 1 I 請 ί 1 遒 原 鐵 者 <? 先 閱 1 I 讀 1 1 6 .如 申 請 專 利 範 圍 第 13項 之 方 法 » 其 中 前 述 還 原 劑 為 含 背 面 1 | 之 I 生 截 者 0 注 意 重 Ί I 1 7 ·如 串 請 專 利 範 園 第 13項 之 方 法 1 其 中 前 述 m 原 爾 為 由 爭 項 再 丄 峰 c 鐵 — 矽 合 金 > 钛 一 矽合 金 、 鈦 一 鋁 合 金 、 鋅 — 鋁 合 金 馬 本 k 頁 1 、 錳 — 鎂 合 金 > 鋁 -鋅 — 钙 合 金 鋁 — 賜 合 金 鋁 — 1 矽 合 金 鎂 — 錳 合 金、 及 鈣 — 矽 合 金 之 群 體 中 選 擇 的 1 至 少 1 種 者 0 1 1 1 8 .如 申 請 專 利 範 tag* 圃 第 13項 之 方 法 > 其 中 刖 述 m 原 劑 為 水 訂 1 溶 性 化 合 物 者 〇 1 I 1 9 .如 申 請 專 利 範 園 第 18項 之 方 法 » 其 中 刖 述 遢 原 劑 為 有 I I 機 酸 或 其 衍 生 物 次磷 酸 或 其 衍 生 物 或 硫 化 塩 者 0 « | 20 .如 申 請專利範園第1 3項 之 方 法 1 其 中 前 逑 m 原 劑 為 含 1 粒徑5 0 0 u m Μ 下 之 粉末 者 〇 1 I 2 1 . — 捶 因 鹵 化 有 機 化 物污 染 的 污 染 物 之 淨 化 方 法 t 該 方 1 1 法 中 具 有 將25υ 下 對摞 準 氫 電 棰 之 標 準 電 極 電 位 130® V 1 1 - 2 400bV之遢原劑、及從賵營養型厭氣性微生物之營 1 I 養 源 > 添 加 於 前 述 污染 物 中 之 步 驟 i 而 其 刖 述 營 養 游 1 I 為有機態碳 、 及 含 前述 有 機 態 碳 之 25重 量 % 的 氧 化 態 1 ί I 氮 者 0 1 1 22 .如 申 讅 專 利 範 圃 第21項 之 方 法 9 其 中 前 述 營 養 源 為 含 1 1 本紙張尺度適用中國國家梯準(CNS ) A4規格(210X297公釐) 66 39498 43 86 2 1 D8 經濟部中央標準局員工消費合作社印製 J 六、申請專利範圍 1 I Ί,ίίι 月[J 述 有 桷 態 碳 之 2 0 〜30重 量 % 之 氧 化 態 氮 者 〇 1 I 2 3 ·如 串 請 專 利 範 圍 第 21項 之 方 法 其 中 » J. 刖 述 有 櫬 態 碳 由 1 ί 水 溶 液 性 有 機 碳 源 供應 者 0 1 I 請 1 I 24 ·如 串 請 專 利 範 園 第 21項 之 方 法 1 其 中 刖 述 % 原 劑 為 先 閱 1 I 讀 1 25它 下 對 標 準 氬 電 極之 標 準 電 極 電 位 為 -400aV 背 1¾ I 之 ; -2 400b V之金靨物質者。 注 意 I 25 ·如 請 專 利 範 圍 第 21項 之 方 法 1 其 中 前 述 % 原 劑 為 由 Ψ 項 再 1 I 填 C 埋 原 嫌 生 m 、 嫌 一砂 合 金 鈦 一 合 金 、 鋅 合 金 Λ 錳 寫 本 裝 頁 1 合 金 鋁 合 金 鎂 合金 > 及 鈣 合 金 之 群 體 中 m 擇 的 至 1 少 1 種 者 0 1 1 26 .如 請 専 利 範 園 第21項 之 方 法 1 其 中 刖 述 m 原 劑 為 水 [ 1 溶 性 化 合 物 者 0 訂 1 27 ·如 申 請 專 利 範 _ 第21項 之 方 法 * 其 中 X f.· 月『J 述 m 原 劑 為 含 1 I 粒徑500m a K 下 粉 末者 〇 1 I 2 8 · — 種 因 含 鹵 化 有 機 化合 物 及 固 艚 污 染 的 污 染 物 之 淨 化 Μ 方 法 9 該 方 法 具 有 將從 羼 營 養 型 厭 氣 性 微 生 物 曾 着 源 與 水 之 營 養 液 * 及在25υ 下 對 檷 準 氫 霣 極 之 標 準 轚 極 1 1 電 位 為 130®V- 2400nV之堪原 劑 與 前 述 污 染 物 混 合 之 I 1 步 驟 1 此 ,1 月(J 述 混 合 步嫌 並 具 有 調 整 刖 逑 污 染 物 於 ΡΗ4 . 5 1 1 9 . 0範圃之步驟; 及將前述混合物靜置於低通氣條件 i 下 之 步 驟 〇 1 1 ϊ 29 .如 請 專 利 範 圃第28項 之 方 法 1 其 中 Λ ft 刖 述 适 原 繭 為 粉 1 1 末 形 態 * 將 刖 述 營 着液 添 加 於 刖 述 污 染 物 中 混 合 之 後, 1 1 再 將 前 述 缠 原 劑 添 加於 刖 述 棍 合 物 中 t 然 後 再 將 其 混 1 1 本紙張尺度適用中國國家標準(CNS ) A4規格(210X297公釐) 67 3 9 4 9 8 Cd D〇 六、申請專利範圍 合。 30. 如申請專利範匾第28項之方法,其中前述遒原劑為具 有粒徑5 0 0 W b Μ下粉末者。 31. 如申請專利範圃第28項之方法,其中前述遒原劑為由 還原鐵、生鐵、鐵一矽合金、鈦合金、鋅合金、錳合 金、鋁合金、鎂合金、及鈣合金之群體中_擇的至少 1種者。 32. 如申請專利範匾第28項之方法,其第1階段步驟在前 述污染物中添加、混合前述污染物量之1〜10 vol%的 前述營養液,其次並有2種在前述污染物中添加、琨 合較第1階段中添加量更大量之前述營養液。 33. 如申讅専利範園第28項之方法,其第1階段步鼸為在 前述污染物中添加、混合前述污染物量之1〜5 vol% 的前述營養液,第2階段步驟為在前述污染物中添加 、混合與第1階段合計為前述污染物5〜10 vol%之前 述曾養液,並有工程在前述污染物中添加、混合比第 1階段或第2階段添加量更大最之前述營着液者。 經濟部中央標隼局員工消費合作社印製 (請先閲讀背面之注意事項再填寫本頁) 訂 34. 如申請專利範園第28項之方法,其中前述堪原劑為水 溶性化合物,而前述道原劑溶解於前述營養液中者。 35. 如申請専利範圍第28項之方法,其前述靜置步驟中, 前述污染物至少在最初之3日內保持於17〜6010者。 本紙張尺度適用中國國家標準(CNS ) A4規格(210X297公釐) 68 3 9 498Printed by the Consumers' Cooperative of the Central Standards Bureau of the Ministry of Economic Affairs A84386 2 1-88 D8 VI. Application for Patent Scope 1. A method for purifying pollutants contaminated by halogenated organic compounds, the method has the standard electric potential of standard hydrogen electrodes added to 25¾ It is a step of 130biV ~ 2400bV reducing agent and nutrient source of auxotrophic anaerobic microorganisms, wherein the aforementioned primogenizing agent is suitable iron, pig iron, silicon-silicon alloy, titanium alloy, zinc alloy, manganese alloy, aluminum alloy At least one selected from the group of magnesium, magnesium alloy, calcium alloy, and water-soluble compounds. For example, the method of item 1 of the patent application, wherein the aforementioned protonator is a standard electrode potential of a pseudo-hydrogen electrode at 25 t. It is -400®V ~ -2400nV, and it is at least one selected from Riyuan grade, raw iron, iron-silicon alloy, titanium alloy, zinc alloy, manganese alloy, aluminum alloy, magnesium alloy, and calcium alloy. 3. The method of item 1 of Shen Lili Fanpu, in which the above 1 original agent is the one containing the suitable original. 4. The method according to item 1 of the scope of patent application, in which the aforementioned buried original pin is raw W. 5. For the method of applying for the No. 1 item in the Fanli Fanpu, in which the aforementioned rhenium agent is composed of iron-silicon alloy, titanium-silicon alloy, titanium-aluminum alloy, zinc-aluminum alloy, fierce-continuous alloy, Ming-Xin-consumption Alloy, Ming-tin alloy, Ming-silicon alloy, magnesium-manganese alloy, and calcium-silicon alloy. 6. The method according to item 1 of the scope of application, in which the aforementioned rhenium agent is a water-soluble compound. 7. If you apply for the method of item 6 of the Patent Fanyuan, the former 原 ® original agent is available (please read the precautions on the back before filling this page) This paper size applies the Chinese National Standard (CNS) A4 specification ( (210 X 297 mm) 64 3 9 49 8 ABCD 4386 21 6. Apply for a patent of dry organic acid or its derivative, hypophosphorous acid or its derivative, or a compound of halide. (Please read the precautions on the back before filling out this page) 8. If you apply for the method of No. 1 plaque, the aforementioned rhenium agent is a powder with a particle size of 500 # b or less. 9. The method according to Shen Lili Fan_ Item 1, wherein the water content of the aforementioned pollutants is at least 25% by weight. 10. For the method of Shenyang Patent Fanyuan Item 1, after the aforementioned adding step, there is another step of maintaining the aforementioned pollutants in the range of pH 4.5 to 9.0 to promote the dehalogenation of the aforementioned halogenated halogenated compounds. . 11. For the method of applying for the first item of the patent park, after the above-mentioned adding step, there is another step of maintaining the aforementioned pollutants at the range of pH 4.5 ~ 9.0 and the original environment. 12. For the method of applying for the first item of the Lili Garden, there is a step of adding various compost, composted organic matter, or organic matter-containing waste water and waste to the above-mentioned sewage beam, and then mixing them. 13. —A method for purifying pollutants contaminated by halogenated organic compounds, the method has a potential of 13C at 25C to a standard hydrogen electrode. ~~~~~~~~~~~~~~~~~~~~~~~~~ The step of adding 0 m V of the phytogenic agent to the aforementioned pollutants, wherein the aforementioned strontium is composed of "original iron, raw iron, silicon-silicon alloy, titanium alloy, zinc alloy, manganese alloy, aluminum alloy, magnesium alloy, Calcium alloy and water-soluble compounds are buried in 1 μM. 14. The method according to item 13 of the scope of patent application, wherein the potential of the aforementioned rhenium agent to the quasi-hydrogen quasi-electrode at 25t: -400bV ~ -2400HV, and the reason is based on the original iron, raw intercept, A silicon alloy and titanium alloy. The paper size is applicable to China National Standards (CNS) A4 (210 X 297 mm) 65 3 9 4 9 8 438621 Employees of the Central Standards Bureau of the Ministry of Economic Affairs have printed the D0 hole and applied for patents. 1 I Zinc alloy, manganese alloy, aluminum alloy, magnesium alloy% and at least one of m 1 1 1 selected in the aluminum alloy 1 1 1 1 5. For example, the method of the 13th item of the patent application Meiyuan 9 In which the original agent is described To include ^ ~, 1 I please 1 1 遒 原 铁 者 <? Read 1 I read 1 1 6. The method of applying for the scope of the patent item 13 »Where the aforementioned reducing agent is I with the back 1 | 0 Attention repetition I 1 7 · If you ask, please refer to Item 13 of the Patent Fan Garden Method 1 where the foregoing m original is due to the repetition of the peak c iron-silicon alloy> titanium-silicon alloy, titanium-aluminum alloy, zinc-aluminum alloy Maben k page 1, manganese-magnesium alloy> aluminum- Zinc—Calcium alloy—Aluminium alloy— 1 Silicon alloy—Magnesium—Manganese alloy, and Calcium—Silicon alloy. At least one of these is selected. 0 1 1 1 8. Method > Where the original m agent is water-soluble 1 soluble compound 〇1 I 1 9. The method of the patent application No. 18 »Where the original magenta agent is II organic acid or its derivative hypophosphorous acid Or its derivatives or vulcanized vulcanizates 0 «| 20. For example, method 1 of Patent Application No. 13 of the Patent Application 1, where the former 逑 m original agent is a powder containing 1 with a particle size of 50 0 um 〇 0 I 2 1 . — Quinine halogenated Purification method for pollutants contaminated by chemical compounds. The method 1 of this method has a standard electrode potential of 25 volts against quasi-hydrogen, 130® V 1 1-2 400bV, and a nutrient-type anaerobic property. Camp of Microorganisms 1 I Nutrient > Step i added to the aforementioned pollutant and its stated nutrient swim 1 I is organic carbon and an oxidation state 1 containing 25% by weight of the aforementioned organic carbon 1 ί I nitrogen 1 1 22. The method of item 21 of Shenyang Patent Fanpu 9 where the aforementioned nutrient source contains 1 1 This paper size is applicable to China National Standard (CNS) A4 (210X297 mm) 66 39498 43 86 2 1 D8 Economy Printed by the Consumer Standards Cooperative of the Ministry of Standards of the People's Republic of China J. Application scope of patents 1 I Ί, ίι 月 [J Describing 2 to 30% by weight of nitrogen in the form of carbon in the form of oxidized nitrogen 〇1 I 2 3 Method of scope item 21 of which »J. states that the carbon is supplied from an aqueous organic carbon source 0 1 I Please 1 I 24 · If you ask for the method of the 21st paragraph of the patent fan garden 1 where the% of the original agent is read first 1 I read 1 25 The standard electrode potential for the standard argon electrode is -400aV back 1¾ I of; -2 400b V of gold tincture. Note I 25 · If method 1 of the scope of the patent is requested, the above 1% of the original agent is from item 再 and then 1 I fill in the original susceptible m, susceptible to a sand alloy titanium-alloy, zinc alloy Λ manganese writing book 1 Alloys, aluminum alloys, magnesium alloys, and calcium alloys in the group of m at least 1 selected 0 1 1 26. For example, please refer to the method of item 21 of the Li Fanyuan, where the m agent is water [1 soluble compound 0 for 1 27 • Method of applying for patent _ item 21 method * where X f. · Month "J s m original agent is powder containing 1 I particle size 500 m a K 0 1 I 2 8 · — cause Purification of halogen-containing organic compounds and solid-contaminated pollutants Method 9 This method has a standard for hydrating anaerobic microorganisms and water in nutrient solutions * and a standard of quasi-hydrogen at 25 ° Pole 1 1 Mixture of a potential agent with a potential of 130®V- 2400nV and the aforementioned pollutants 1 1 Step 1 This (1) (1) (1) The mixing step is suspected and the pollutants have to be adjusted to pH 4. 5 1 1 9. 0 Fan Pu Steps; and the step of statically aerating the aforementioned mixture under low aeration conditions i 0 1 1 ϊ 29. For example, please refer to the method 1 of the patent range 28, where Λ ft states that the original cocoon is powder 1 1 and the final form * will be After the narrative solution is added to the narrative pollutants, 1 1 is added to the narrative stick compound t, and then mixed 1 1 This paper size applies the Chinese National Standard (CNS) A4 Specifications (210X297 mm) 67 3 9 4 9 8 Cd D06. The scope of patent application is in line. 30. The method according to item 28 of the patent application plaque, wherein the aforementioned protogen is a powder having a particle size of 500 W b M. 31. The method according to item 28 of the patent application, wherein the aforementioned rhenium agent is a group consisting of reduced iron, pig iron, iron-silicon alloy, titanium alloy, zinc alloy, manganese alloy, aluminum alloy, magnesium alloy, and calcium alloy. At least one of the _ selected. 32. For the method of claim 28 in the patent application, the first step of the method is to add and mix the aforementioned nutrient solution in an amount of 1 to 10 vol% of the amount of the aforementioned pollutants, followed by 2 kinds of the aforementioned pollutants. The nutrient solution is added and blended in a larger amount than in the first stage. 33. The method of item 28 of Shenyang Lifan Garden, the first step of which is to add and mix the aforementioned nutrient solution in an amount of 1 to 5 vol% of the amount of the aforementioned pollutants, and the second step is to perform the aforementioned steps Addition, mixing and first stage of the pollutants are 5 ~ 10 vol% of the aforementioned former nutrient solution, and there are projects that add and mix the aforementioned pollutants in a larger amount than the first stage or the second stage. The aforementioned campers. Printed by the Consumers' Cooperative of the Central Bureau of Standards, Ministry of Economic Affairs (please read the precautions on the back before filling out this page). Revision 34. For the method of applying for Patent No. 28, where the aforementioned primogenogen is a water soluble compound and Daoyuan agent is dissolved in the aforementioned nutrient solution. 35. If the method of applying for benefit range item 28 is applied, in the aforementioned standing step, the aforementioned pollutants are maintained at 17 ~ 6010 for at least the first 3 days. This paper size applies to China National Standard (CNS) A4 (210X297 mm) 68 3 9 498
TW87101140A 1997-02-07 1998-01-26 Purification method for contaminants caused by halogenated organic compounds TW438621B (en)

Applications Claiming Priority (5)

Application Number Priority Date Filing Date Title
JP02536797A JP4021511B2 (en) 1997-02-07 1997-02-07 Purification method for organic chlorine compound contaminants
JP16439997 1997-06-20
JP21206997 1997-08-06
JP27457597 1997-10-07
JP31059997 1997-11-12

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
TWI551551B (en) * 2010-04-30 2016-10-01 三菱瓦斯化學股份有限公司 Peroxide activator and method for purifying soil and/or underground water

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
TWI551551B (en) * 2010-04-30 2016-10-01 三菱瓦斯化學股份有限公司 Peroxide activator and method for purifying soil and/or underground water

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