TWI238148B - Method for treating fluoride containing waste water - Google Patents
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- TWI238148B TWI238148B TW91125107A TW91125107A TWI238148B TW I238148 B TWI238148 B TW I238148B TW 91125107 A TW91125107 A TW 91125107A TW 91125107 A TW91125107 A TW 91125107A TW I238148 B TWI238148 B TW I238148B
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1238148 _案號91125107_年月曰 修正___ 五、發明說明(1) 發明領域 本發明是有關於一種廢水處理方法,且特別是有關於 一種含氟廢水之處理方法。 發明背景 在工業活動中,例如玻璃製造、電鑛操作、鋁及鋼的 煉製、半導體元件之製造等,皆在製造過程中大量使用氟 化物,因而在其排放廢水中也會含有大量氟離子。為了避 免氟離子污染環境,因此必須對上述製程之排放廢水進行 適當之處理,以移除排放廢水中之氟離子。 習知移除含氟廢水中氟離子之方法係為鈣化合物混凝 沈澱法。此種方法係利用鈣化合物(包括氫氧化鈣(C a ( Ο Η ) 2、氯化鈣(CaCl2)等)使氟離子變成非溶解性氟化鈣(CaF2) 沈澱而移除之。目前,業界常使用之鈣化合物混凝沈澱法 包括氯化鈣混凝沈澱模式(稱為純氯化鈣模式)與氫氧化鈣 混凝沈殿模式(稱為石灰模式)。 就氯化鈣混凝沈澱模式而言,首先將含氟廢水導入中 和槽中,並以氫氧化納中和含氟廢水使其酸驗值為p Η值7 〜8左右後,再將ρ Η值7〜8之含氟廢水導入反應槽中,然 後於反應槽中加入氯化鈣溶液,使含氟廢水中之氟離子與 氯化鈣反應形成氟化鈣結晶。然後,將含氟廢水導入混擬 沈澱槽中,並依序利用助凝劑(P A C )與高分子沈降劑使氟 化鈣結晶凝集、沈降,並從混擬沈澱槽之上部部位排放澄 清廢水。而留在混擬沈澱槽下方之氟化鈣沈澱物則利用污 泥餅機脫水形成氟化鈣污泥,以達成將氟離子從廢水中脫 去之目的。1238148 _Case No. 91125107_ Year Month Amendment ___ V. Description of the Invention (1) Field of the Invention The present invention relates to a method for treating wastewater, and more particularly to a method for treating fluorine-containing wastewater. BACKGROUND OF THE INVENTION In industrial activities, such as glass manufacturing, electricity and mining operations, aluminum and steel refining, and semiconductor component manufacturing, a large number of fluorides are used in the manufacturing process, so a large amount of fluoride ions are also contained in their discharged wastewater. . In order to avoid the pollution of fluoride ion by the environment, the waste water from the above process must be properly treated to remove the fluoride ion from the waste water. The conventional method for removing fluoride ions from fluorine-containing wastewater is the coagulation precipitation method of calcium compounds. This method uses calcium compounds (including calcium hydroxide (C a (Ο Η) 2, calcium chloride (CaCl2), etc.)) to remove fluoride ions into precipitates of insoluble calcium fluoride (CaF2) and removes them. Currently, The calcium compound coagulation precipitation method commonly used in the industry includes calcium chloride coagulation precipitation mode (called pure calcium chloride mode) and calcium hydroxide coagulation Shendian mode (called lime mode). For example, first introduce the fluorine-containing wastewater into the neutralization tank, and neutralize the fluorine-containing wastewater with sodium hydroxide so that the acid test value is p Η value of 7 to 8, and then ρ Η value of 7 to 8 fluorine Wastewater is introduced into the reaction tank, and then calcium chloride solution is added to the reaction tank, so that fluoride ions in the fluorine-containing wastewater react with calcium chloride to form calcium fluoride crystals. Then, the fluorine-containing wastewater is introduced into the mixed precipitation tank, and Using coagulant (PAC) and polymer sedimentation agent in order to agglomerate and settle the calcium fluoride crystals, and discharge clarified wastewater from the upper part of the mixed sedimentation tank. The calcium fluoride precipitates left under the mixed sedimentation tank The sludge cake machine is used to dehydrate to form calcium fluoride sludge to achieve The purpose of fluoride ion removal from wastewater.
9953 t.wf 1. ptd 第5頁 1238148 _案號 91125107_年月日_ 五、發明說明(2) 就氫氧化鈣混凝沈澱模式而言,則使用氫氧化鈣取代 氯化鈣。以氫氧化鈣取代氯化鈣之優點在於氫氧化鈣本身 可提供#5離子(Ca2 + )及兩當量之氫氧根離子(OH —),因此 在藥品上可減少氫氧化鈉之使用,而不需要設置中和槽。 但是,氫氧化鈣藥品較氯化鈣藥品貴,而且氫氧化鈣模式 之加藥控制不易,因此目前業界比較少使用。 然而,對於上述移除含氟廢水中氟離子之方法而言, 由於製程之關係,在一般半導體廠之含氟廢水中,除了氟 離子外,通常亦含有可觀的其他酸液(如硫酸、硝酸及磷 酸等),因此當添加氫氧化鈣或氯化鈣於廢水系統中時, 除了產生氟化鈣結晶之外,鈣離子亦會與其他酸根離子產 生反應而形成硫酸鈣、硝酸鈣、磷酸鈣等化合物沈澱。若 處理控制不當,有可能添加氫氧化鈣或氯化鈣於廢水系統 後,鈣離子先與硫酸根離子、硝酸根離子、磷酸根離子反 應形成硫酸鈣、硝酸鈣、磷酸鈣等化合物,然後鈣離子才 與氟離子形成氟化鈣,因而浪費氫氧化鈣或氯化鈣。 而且,就上述移除含氟廢水中氟離子之方法而言,硫 酸鈣、硝酸鈣、磷酸鈣等化合物沈澱之生成,也會造成整 個含氟廢水處理製程的污泥量增加,而提高處理污泥之成 本。因此,如何達成污泥減量是很重要的。 發明概要 有鑑於此,本發明之一目的為提供一種含氟廢水之處 理方法,能夠減少氯化鈣之使用量、減少污泥量、並且所 排放廢水中之氟離子濃度亦低於法規標準。 本發明提供一種含氟廢水之處理方法,此方法係先進9953 t.wf 1. ptd Page 5 1238148 _ Case No. 91125107_ Year Month_ V. Description of the invention (2) In the case of calcium hydroxide coagulation precipitation mode, calcium hydroxide is used instead of calcium chloride. The advantage of replacing calcium chloride with calcium hydroxide is that calcium hydroxide itself can provide # 5 ion (Ca2 +) and two equivalent hydroxide ion (OH —), so it can reduce the use of sodium hydroxide in medicine, and There is no need to set a neutralization tank. However, calcium hydroxide medicines are more expensive than calcium chloride medicines, and the addition of calcium hydroxide is not easy to control. Therefore, the industry is currently less used. However, for the above-mentioned method for removing fluorine ions in fluorine-containing wastewater, due to the manufacturing process, in general fluorine-containing wastewater in semiconductor factories, in addition to fluoride ions, it usually contains considerable other acid solutions (such as sulfuric acid, nitric acid, etc.). And phosphoric acid), so when calcium hydroxide or calcium chloride is added to the waste water system, in addition to generating calcium fluoride crystals, calcium ions will also react with other acid ions to form calcium sulfate, calcium nitrate, and calcium phosphate. And so on. If the treatment is not controlled properly, it is possible to add calcium hydroxide or calcium chloride to the waste water system. The calcium ion first reacts with sulfate ion, nitrate ion, and phosphate ion to form compounds such as calcium sulfate, calcium nitrate, calcium phosphate, and then calcium. Only the ions form fluoride with the fluoride ions, thus wasting calcium hydroxide or calcium chloride. In addition, as for the method for removing fluorine ions in the fluorine-containing wastewater, the precipitation of compounds such as calcium sulfate, calcium nitrate, and calcium phosphate will also cause an increase in the amount of sludge in the entire fluorine-containing wastewater treatment process and improve the treatment of sewage. The cost of mud. Therefore, how to achieve sludge reduction is very important. SUMMARY OF THE INVENTION In view of this, an object of the present invention is to provide a method for treating fluorine-containing wastewater, which can reduce the amount of calcium chloride used, reduce the amount of sludge, and the concentration of fluorine ions in the discharged wastewater is lower than the regulatory standard. The invention provides a method for treating fluorine-containing wastewater, which is an advanced method.
9953t.wfl.ptd 第6頁 1238148 _案號91125107_年月曰 修正__ 五、發明說明(3) 行反應處理步驟,於已導入含氟廢水之第一反應槽中加入 氫氧化#5與氯化舞之混和溶液,並調整第一反應槽内之含 氟廢水之酸鹼值(pH值)為2至5左右,以使鈣離子與含氟廢 水中之氟離子生成氟化鈣。接著,進行混凝沈澱處理步 驟,將含氟廢水導入混凝沈澱槽,並於混凝沈澱槽加入氫 氧化鈉溶液與助凝劑,以調整混凝沈澱槽内之含氟廢水之 酸鹼值(p Η值)為7至8左右,並使氟化#5混凝沈澱下來。然 後進行廢水排放步驟,從混擬沈澱槽之上部部位排放澄清 廢水,並進行污泥處理步驟,將留在混擬沈澱槽中之氟化 鈣沈澱物脫水形成氟化鈣污泥。 上述反應處理步驟更包括將含氟廢水導入第二反應 槽,然後於第二反應槽中加入氫氧化鈣與氯化鈣之混和溶 液,並調整第二反應槽内之含氟廢水之酸鹼值(ρ Η值)為2 至5左右,以使鈣離子與含氟廢水中之氟離子生成氟化 !弓。 而且,上述混凝沈澱步驟中更包括加入高分子沈降劑 於含氟廢水中,使氟化鈣混凝沈澱下來。 本發明係利用在酸環境下(在酸鹼值(ρ Η值)為2至5左 右)鈣離子會與氟離子反應形成氟化鈣而沈澱出來,但是 鈣離子卻不會與其他之酸根離子如硫酸根離子、硝酸根離 子、磷酸根離子等反應形成硫酸鈣、硝酸鈣與磷酸鈣等而 沈澱出來之原理。在反應處理步驟中調整含氟廢水之酸鹼 值(ρ Η值)為2至5左右,使得氟離子先從廢水中析出,因此 可以有效的降低廢水中氟離子的含量。 而且,因為大部分之鈣離子已先與氟離子反應而沈澱9953t.wfl.ptd Page 6 1238148 _Case No. 91125107_ Year Month Amendment __ V. Description of the invention (3) Perform a reaction treatment step, and add hydroxide # 5 and The mixed solution of chlorinated dance and adjusted the acid-base value (pH value) of the fluorine-containing wastewater in the first reaction tank to about 2 to 5, so that calcium ions and fluorine ions in the fluorine-containing wastewater generate calcium fluoride. Next, a coagulation sedimentation treatment step is performed, and the fluorine-containing wastewater is introduced into the coagulation sedimentation tank, and sodium hydroxide solution and a coagulant are added to the coagulation sedimentation tank to adjust the pH value of the fluorine-containing wastewater in the coagulation sedimentation tank. (P Η value) is about 7 to 8, and fluorinated # 5 is coagulated and precipitated. Then, a wastewater discharge step is performed to discharge clarified wastewater from the upper part of the mixed sedimentation tank, and a sludge treatment step is performed to dehydrate the calcium fluoride precipitate remaining in the mixed sedimentation tank to form calcium fluoride sludge. The above reaction treatment step further includes introducing the fluorine-containing wastewater into the second reaction tank, and then adding a mixed solution of calcium hydroxide and calcium chloride to the second reaction tank, and adjusting the acid-base value of the fluorine-containing wastewater in the second reaction tank. (Ρ Η value) is about 2 to 5 so that calcium ion and fluoride ion in the fluorine-containing wastewater generate fluoride! Bow. Moreover, the above coagulation and precipitation step further includes adding a polymer sedimentation agent to the fluorine-containing wastewater to coagulate and precipitate calcium fluoride. In the present invention, in an acid environment (at an acid-base value (ρ Η value) of about 2 to 5), calcium ions will react with fluoride ions to form calcium fluoride and precipitate out, but the calcium ions will not react with other acid ions. Such as the sulfate ion, nitrate ion, phosphate ion and other reactions to form calcium sulfate, calcium nitrate and calcium phosphate, etc. and the principle of precipitation. In the reaction treatment step, the acid-base value (ρ Η value) of the fluorine-containing wastewater is adjusted to about 2 to 5, so that the fluoride ions are first precipitated from the wastewater, so the content of fluorine ions in the wastewater can be effectively reduced. Moreover, because most of the calcium ions have reacted with the fluoride ions to precipitate
9953t.wfl.ptd 第7頁 1238148 _案號91125107_年月日_iti_ 五、發明說明(4) 出來,而剩餘的鈣離子才會在後續之混凝沈澱製程中與硫 酸根離子、硝酸根離子、磷酸根離子等形成硫酸鈣、硝酸 鈣與磷酸鈣等沈澱。所以本發明之方法不但可以有效的移 除氟離子,還可以減少鈣化合物用量與含氟廢水處理製程 之污泥量,而可以節省成本。 為讓本發明之上述和其他目的、特徵、和優點能更明 顯易懂,下文特舉一較佳實施例,並配合所附圖式,作詳 細說明如下: 圖式之標示說明: 1 ◦ 0 :廢水 1 0 2、1 ◦ 6 :反應槽 1 0 4 :辦化合物混和溶液 1 0 8 :混凝沈澱槽 1 1 0 :快混槽 1 1 4 :沈降槽 1 1 6 :濃縮槽 1 1 8 :助凝劑 1 2 0 :中和劑 1 2 2 :高分子沈降劑 較佳實施例之說明 本發明之含氟廢水之處理方法係在反應處理步驟中, 藉由調整含氟廢水之酸驗值(pH值)為2至5左右,使得#5離 子只會與氟離子形成氟化鈣,而不會與其他的酸根離子形 成化合物沈澱,因此可以有效的降低廢水中氟離子的含 量,並且減少鈣化合物用量與含氟廢水處理製程之污泥9953t.wfl.ptd Page 7 1238148 _Case No. 9125107_year month_iti_ V. Description of the invention (4), and the remaining calcium ions will be combined with sulfate ions and nitrate in the subsequent coagulation precipitation process Ions, phosphate ions, etc. form precipitates such as calcium sulfate, calcium nitrate and calcium phosphate. Therefore, the method of the present invention can not only effectively remove fluoride ions, but also reduce the amount of calcium compounds and the amount of sludge in the fluorine-containing wastewater treatment process, and can save costs. In order to make the above and other objects, features, and advantages of the present invention more comprehensible, a preferred embodiment is given below in conjunction with the accompanying drawings to make a detailed description as follows: Symbols of the drawings: 1 ◦ 0 : Wastewater 1 0 2, 1 ◦ 6: Reaction tank 1 0 4: Compound mixing solution 1 0 8: Coagulation sedimentation tank 1 1 0: Quick mixing tank 1 1 4: Settling tank 1 1 6: Concentration tank 1 1 8 : Coagulant 1 2 0: Neutralizer 1 2 2: Description of a preferred embodiment of a polymer precipitant The treatment method of the fluorine-containing wastewater of the present invention is in a reaction treatment step by adjusting the acid test of the fluorine-containing wastewater The value (pH value) is about 2 to 5, so that # 5 ion will only form calcium fluoride with fluoride ion, but will not form compound precipitation with other acid ion, so it can effectively reduce the fluoride ion content in wastewater, and Reduce the amount of calcium compounds and the sludge in the process of fluorine-containing wastewater treatment
9953 t.wf 1. pt.d 第8頁 1238148 _ 案號 91125107 _年月日_修正____ 五、發明說明(5) 量。 本發明之含氟廢水之處理方法至少包括反應處理步 驟、混凝沈澱處理步驟、廢水排放步驟與污泥處理步驟。 以下接著詳細說明本發明之含氟廢水之處理方法。請參照 第1圖所繪示本發明較佳實施例的含氟廢水之處理模式 圖。首先,進行反應處理步驟,將廢水1 〇 〇導入反應槽1 〇 2 中。其中廢水1 0 0除了含有氟化物(如氟酸)之外,還包括 其他廢酸液,其例如是硫酸、硝酸、磷酸等。當廢水1 〇 〇 導入反應槽1 0 2後,於反應槽1 〇 2中加入鈣化合物混和溶液 1 0 4 ’並控制|弓化合物混和溶液1 〇 4之加入量,使反應槽 1 0 2内之廢水1 〇 〇的酸鹼值(ρ η值)例如是維持在為2至5左 右。其中,鈣化合物混和溶液1 〇 4例如是由氫氧化鈣與氯 化鈣所配成之溶液。由於反應槽1 〇 2内之廢水1 〇 〇的酸鹼值 (pH值)例如是為2至5左右,#5離子會較易與廢水1〇〇中之 氟離子結合並形成氟化鈣,而較不易與廢水丨〇〇中之其他 酸根離子如硫酸根離子、硝酸根離子、磷酸根離子等形成 硫酸鈣、硝酸鈣與磷酸鈣等而沈澱出來。 然後’將廢水1 0 0導入另一個反應槽1 q 6,此反應槽 106設置之目的係為避免氟離子於反應槽1〇2中反應不完全 而額外設置的。同樣的,當廢水丨〇 〇導入反應槽丨〇 6後,於 反應槽1 0 6中加入鈣化合物混和溶液丨〇 4,並利用鹽酸 (HC1 )和氫氧化鈉(NaOH)使反應槽106内之廢水的酸鹼值 (ρ Η值)例如是控制在2至5左右,於是廢水丨〇 〇中之氟離子 可進一步的與鈣離子形成氟化鈣。而且,由於反應槽丨〇 6 之廢水的酸鹼值(ρ Η值)仍然維持在2至5左右,因此鈣離子9953 t.wf 1. pt.d page 8 1238148 _ case number 91125107 _ year month day _ amendment ____ 5. Description of the invention (5) Quantity. The method for treating fluorine-containing wastewater of the present invention includes at least a reaction treatment step, a coagulation sedimentation treatment step, a wastewater discharge step, and a sludge treatment step. The following is a detailed description of the method for treating fluorine-containing wastewater of the present invention. Please refer to FIG. 1 for a schematic diagram of a fluorine-containing wastewater treatment mode according to a preferred embodiment of the present invention. First, a reaction treatment step is performed, and waste water 1000 is introduced into the reaction tank 102. The wastewater 100 includes, in addition to fluoride (such as hydrofluoric acid), other waste acid liquids such as sulfuric acid, nitric acid, and phosphoric acid. After the wastewater 100 is introduced into the reaction tank 102, a calcium compound mixed solution 104 is added to the reaction tank 100 and the amount of the bow compound mixed solution 104 is controlled to make the reaction tank 10 The acid-base value (ρ η value) of the wastewater 100 is maintained at about 2 to 5, for example. The calcium compound mixed solution 104 is, for example, a solution prepared from calcium hydroxide and calcium chloride. Since the acid-base value (pH value) of the wastewater 100 in the reaction tank 100 is, for example, about 2 to 5, the # 5 ion will easily combine with the fluoride ions in the wastewater 100 to form calcium fluoride. And it is not easy to form calcium sulfate, calcium nitrate and calcium phosphate with other acid ions such as sulfate ion, nitrate ion, phosphate ion and the like in the wastewater to precipitate out. Then, the waste water 100 is introduced into another reaction tank 1q6. The purpose of setting this reaction tank 106 is to prevent the incomplete reaction of fluoride ions in the reaction tank 102, and it is additionally provided. Similarly, after the wastewater is introduced into the reaction tank, the calcium compound mixed solution is added to the reaction tank 106, and the reaction tank 106 is made of hydrochloric acid (HC1) and sodium hydroxide (NaOH). The acid-base value (ρ Η value) of the wastewater is, for example, controlled at about 2 to 5, so that fluoride ions in the wastewater can further form calcium fluoride with calcium ions. In addition, since the pH value of the wastewater in the reaction tank 丨 〇6 is still maintained at about 2 to 5, the calcium ion
9953t.wfl.ptd 第9頁 1238148 _案號91125107_年月曰 修正_^ 五、發明說明(6) 較不易與廢水中之其他酸根離子如硫酸根離子、硝酸根離 子、磷酸根離子等形成硫酸鈣、硝酸鈣與磷酸鈣等。 接著,進行混凝沈澱處理步驟,將廢水1 0 0導入混凝 沈澱槽1 0 8中。混凝沈澱槽1 0 8至少包括快混槽1 1 0、慢混 槽1 1 2、沈降槽1 1 4與濃縮槽1 1 6。當廢水1 0 0導入快混槽 1 1 0時,於快混槽1 1 0中加入助凝劑1 1 8 (助凝劑包括鋁鹽 (P AC ),其例如是氯化鋁等),並於快混槽1 1 0中加入中和 劑1 2 0 (中和劑1 2 0例如是氫氧化鈉)使廢水1 0 0之酸鹼值(p Η 值)調整為例如是7至8左右,以進行混凝吸附沈澱反應, 生成白色氫氧化紹與氟化#5共沈澱物。而且,當廢水1 0 0 之酸鹼值(ρ Η值)上升至7至8左右時,廢水1 0 0中之剩餘的 鈣離子會與廢水1 0 0中之其他酸根離子如硫酸根離子、硝 酸根離子、磷酸根離子等形成硫酸鈣、硝酸鈣與磷酸鈣等 而沈澱出來。這些硫酸鈣、硝酸鈣與磷酸鈣等沈澱物也會 與氫氧化鋁形成共沈澱物。 然後,廢水1 0 0再導入慢混槽1 1 2中,並於慢混槽1 1 2 中加入高分子沈降劑1 2 2,以使廢水1 0 0中之氟化鈣、硫酸 鈣、硝酸鈣與磷酸鈣等沈澱物進一步的凝聚在一起。接 著,廢水1 0 0在依序導入沈降槽1 1 4與濃縮槽1 1 6中使污泥 凝集沈澱下來。 之後,進行廢水排放步驟與污泥處理步驟,當廢水 1 0 0中之污泥在混擬沈澱槽1 0 8中混凝沈澱下來後,從混擬 沈澱槽1 0 8之上部部位排放澄清廢水,而留在混擬沈澱槽 1 0 8中之氟化鈣沈澱物則利用污泥餅機脫水形成氟化鈣污 泥,以達成將氟離子從廢水中脫去之目的。其中,經過本9953t.wfl.ptd Page 9 1238148 _Case No. 9125107_Year Month Amendment_ ^ V. Description of the invention (6) It is not easy to form with other acid ion such as sulfate ion, nitrate ion, phosphate ion, etc. in wastewater Calcium sulfate, calcium nitrate and calcium phosphate. Next, a coagulation and sedimentation treatment step is performed, and the wastewater 100 is introduced into the coagulation and sedimentation tank 108. The coagulation sedimentation tank 1 0 8 includes at least a fast mixing tank 1 10, a slow mixing tank 1 1 2, a sedimentation tank 1 1 4 and a concentration tank 1 16. When wastewater 100 is introduced into the fast mixing tank 1 110, a coagulant 1 1 8 is added to the fast mixing tank 1 10 (the coagulant includes an aluminum salt (P AC), which is, for example, aluminum chloride, etc.), A neutralizer 1 2 0 (the neutralizer 1 2 0 is, for example, sodium hydroxide) is added to the fast mixing tank 1 10 to adjust the pH (p Η value) of the wastewater 1 0 to, for example, 7 to 8 Left and right to carry out the coagulation adsorption precipitation reaction, and generate a white precipitate of co-precipitation of white hydroxide and fluorinated # 5. Moreover, when the acid-base value (ρ Η value) of the wastewater 100 rises to about 7 to 8, the remaining calcium ions in the wastewater 100 and other acid ions such as sulfate ions, Nitrate ions, phosphate ions, etc. form calcium sulfate, calcium nitrate, calcium phosphate, etc. and precipitate out. These precipitates such as calcium sulfate, calcium nitrate and calcium phosphate also form co-precipitates with aluminum hydroxide. Then, the waste water 100 is re-introduced into the slow mixing tank 1 12 and a polymer sedimentation agent 1 2 2 is added to the slow mixing tank 1 12 to make calcium fluoride, calcium sulfate, nitric acid in the waste water 100 Calcium is further aggregated with precipitates such as calcium phosphate. Next, the wastewater 100 is sequentially introduced into the sedimentation tank 1 1 4 and the concentration tank 1 16 to cause the sludge to aggregate and settle. After that, a wastewater discharge step and a sludge treatment step are performed. When the sludge in the wastewater 100 is coagulated and settled in the mixed sedimentation tank 108, the clarified wastewater is discharged from the upper part of the mixed sedimentation tank 108. The calcium fluoride precipitate remaining in the mixed precipitation tank 108 is dehydrated by a sludge cake machine to form calcium fluoride sludge, so as to achieve the purpose of removing fluoride ions from the wastewater. Among them, after this
9953t.wfl.ptd 第10頁 1238148 _案號91125107_年月日__ 五、發明說明(7) 發明之方法處理後之廢水1 0 0中之氟離子含量可以降至 1 5 ppm以下,而低於法規標準。而且污泥量與習知的方法 相比較可減少2 0 %〜3 0 %以上。 依照本發明實施例所述,本發明係利用在酸環境下 (在酸鹼值(pH值)為2至5左右)鈣離子較易與氟離子反應形 成氟化鈣而沈澱出來,而較不易與其他之酸根離子如硫酸 根離子、硝酸根離子、磷酸根離子等反應之原理來減少氯 化鈣之使用量,並減少污泥量。而在反應處理步驟中調整 含氟廢水之酸鹼值(pH值)為2至5左右,使得氟離子先從廢 水中析出,因此可以有效的降低廢水中氟離子的含量。 而且,因為大部分之鈣離子已先與氟離子反應而沈澱 出來,而剩餘的鈣離子才會在後續之混凝沈澱製程中與硫 酸根離子、硝酸根離子、磷酸根離子等形成硫酸鈣、硝酸 鈣與磷酸鈣等沈澱。所以本發明之方法不但可以有效的移 除氟離子,還可以減少鈣化合物用量與含氟廢水處理製程 之污泥量,而可以節省成本。 而且在上述實施例係以設置兩個反應槽為實例做說 明,而第二個反應槽係為輔助之用,以將未在第一個反應 槽形成氟化鈣之氟離子析出。當然。本發明也可以視實際 需要而只設置一個反應槽或兩個以上之反應槽。 雖然本發明已以較佳實施例揭露如上,然其並非用以 限定本發明,任何熟習此技藝者,在不脫離本發明之精神 和範圍内,當可作各種之更動與潤飾,因此本發明之保護 範圍當視後附之申請專利範圍所界定者為準。9953t.wfl.ptd Page 10 1238148 _Case No. 9125107_year month__ V. Description of the invention (7) The content of fluorine ion in wastewater 100 treated by the invention method can be reduced to 15 ppm or less, and Below regulatory standards. Moreover, the amount of sludge can be reduced by more than 20% ~ 30% compared with the conventional method. According to the embodiment of the present invention, in the present invention, it is easier to precipitate calcium fluoride by reacting with fluoride ions to form calcium fluoride in an acid environment (at an acid-base value (pH value) of about 2 to 5), but it is not easy to precipitate out. The principle of reaction with other acid ions such as sulfate ions, nitrate ions, phosphate ions and the like reduces the amount of calcium chloride used and reduces the amount of sludge. In the reaction treatment step, the acid-base value (pH value) of the fluorine-containing wastewater is adjusted to about 2 to 5, so that fluoride ions are first precipitated from the waste water, so the content of fluorine ions in the wastewater can be effectively reduced. In addition, most calcium ions have reacted with fluoride ions to precipitate out, and the remaining calcium ions will form calcium sulfate with sulfate ions, nitrate ions, phosphate ions, etc. in the subsequent coagulation and precipitation process. Precipitation of calcium nitrate and calcium phosphate. Therefore, the method of the present invention can not only effectively remove fluoride ions, but also reduce the amount of calcium compounds and the amount of sludge in the fluorine-containing wastewater treatment process, and can save costs. Moreover, in the above embodiment, two reaction tanks are taken as an example for explanation, and the second reaction tank is used as an auxiliary to precipitate fluorine ions that do not form calcium fluoride in the first reaction tank. of course. According to the present invention, only one reaction tank or two or more reaction tanks may be provided according to actual needs. Although the present invention has been disclosed as above with preferred embodiments, it is not intended to limit the present invention. Any person skilled in the art can make various modifications and retouches without departing from the spirit and scope of the present invention. Therefore, the present invention The scope of protection shall be determined by the scope of the attached patent application.
9953twfl.ptd 第11頁 1238148 案號91125107_年月曰 修正 圖式簡單說明 圖式之簡單說明: 第1圖為繪示之本發明較佳實施例之含氟廢水之處理 模式圖。9953twfl.ptd Page 11 1238148 Case No. 91125107_Year Month Amendment Brief Description of the Drawings Brief Description of the Drawings: Figure 1 is a schematic diagram showing the treatment of fluorine-containing wastewater in a preferred embodiment of the present invention.
9953t.wfl.ptd 第12頁9953t.wfl.ptd Page 12
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TWI577642B (en) * | 2014-09-22 | 2017-04-11 | 雷賽克實業股份有限公司 | Method of recycling ammonia from wastewater and preparing solid calcium sulfate and calcium chloride solution |
CN114790048A (en) * | 2021-01-26 | 2022-07-26 | 台湾地区“炜业中央投资有限公司” | Method for reducing fluorine content in wastewater by removing heavy metal process by-products |
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TWI577642B (en) * | 2014-09-22 | 2017-04-11 | 雷賽克實業股份有限公司 | Method of recycling ammonia from wastewater and preparing solid calcium sulfate and calcium chloride solution |
CN114790048A (en) * | 2021-01-26 | 2022-07-26 | 台湾地区“炜业中央投资有限公司” | Method for reducing fluorine content in wastewater by removing heavy metal process by-products |
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