TW508264B - Discharge and regeneration system for cogeneration desulfurization device with zero discharge - Google Patents
Discharge and regeneration system for cogeneration desulfurization device with zero discharge Download PDFInfo
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508264 五、發明說明(1) 7¾ # = I月係種八電脫硫設備零排放及再生回收系統, 之@二4種獨特處理程序,而使汽電共生設備燃燒所產生 理呈气5 π ^ 產生3 &I錢之廢水,得被再有效處 德環ΪΓ η液及硫酸詞,且,整體系統之運作,係呈 槌佳之產章=S中不產生廢水排放(零排放)之問題,達到 u之產業利用價值與實用功效。 傳統式之方式及缺點508264 V. Description of the invention (1) 7¾ # = January is a zero discharge and regeneration recovery system of eight electric desulfurization equipment. @ 二 4 kinds of unique processing procedures, so that the gas produced by the cogeneration of gas and electricity symbiosis equipment is 5 π ^ Wastewater that generates 3 & I money can be effectively processed again. Η η liquid and sulfuric acid words, and the operation of the overall system is a good production chapter = no problem of wastewater discharge (zero discharge) in S To achieve the industrial utilization value and practical effect of u. Traditional methods and disadvantages
然晾乾 能轉換為蒸 汽之來源, 故,燃燒過 式對廢氣污 塵或過濾, 方式,係使 /夜」洗條而 液」而留下 ’傳統式之 式處理:彳1 式而取彳|「 方式,皆存 氣與電力 係採用「 程中會有 染之處理 收集廢氣 用於收集 呈「濕式 廢氣中之 方法係將 )自然晾 乾化之污 在有下列 ,係以燃料熱 要’而產生蒸 爐產生蒸汽, 題。而,傳統 經「乾式」集 )。然,此種 水」或「溶 水」或「溶 渴式」處理言 ’亦有三種方 材過濾水等方 泥」;上述之 需極大之「晾乾池」 不符寸土寸金之處。 ’而需極大之場地,However, drying can be converted into the source of steam. Therefore, the burned type can be used to filter or exhaust the exhaust gas, or to filter. | "Methods, both gas and electricity are used." There will be dyed treatment in the process of collecting waste gas for collection of "wet waste gas method is the method of) Drying the pollution naturally has the following, which is based on fuel heat requirements' and The steam produced by the steam oven is a problem. However, the traditional "dry" set). Of course, there are also three types of mud such as filtered water, such as "water-soluble" or "thirsty-thirsty" treatment words; the above-mentioned "drying pond", which requires great amounts, does not match the size of the soil. ’And a huge field is needed,
第6頁 )⑽ 264 )⑽ 264 五、發明說明(2) (2 )加熱蒸乾 (3 )濾材過濾 浪費熱源,且,蒸乾之過程 化物之水蒸氣,雖無「曰產生含硫 但,卻是造成「酸雨」之:煙灰)」, 環境污染。 素’亦是一種 亦需設置壓濾設備,& 濾材(定期更換)、= 2,且需耗用 會阻塞卜亦需定期遠=則 。且’會有廢水排放之困擾:極不方便 綱要 本發明之技術、目的 緣是,本發明乃提供一種前 而可得達到省空間、省資源、广f有之&程方法系統, 功效,其主要技術、目的為··处、速、確實分離之極佳 其一,設有獨特迴路連通之氧化 ^ ^ fr γμ λμ ^ Μ η 鎂貞7 ^、氧化鎂熱解槽、 =叙:槽、吸收塔、氧化槽、底 輸曹、反應槽、氫氧化舞儲 :匕約貯槽、第-沈澱槽、第二沈殿槽、具 爐水封,而得將廢水處理分離呈氫氧化鎂溶液及硫酸 鈣副產物,達到不會有排放廢水二次污染之功效。 /、二,整體系統運作,i自動循環,不會有排放廢水之困 擾。亚’可在節省空間、處理快速之情況,讓汽電共 生設備之廢水處理,達極佳之環保功效。 為讓鈞局貴審核委員及習於此技藝人士,對本發明(Page 6) ⑽ 264 ⑽ ⑽ 264 V. Description of the invention (2) (2) Heating and steaming (3) Filter material wastes heat source, and the steam of the steaming process product has no "sulphur content," It is the cause of "acid rain": soot) ", environmental pollution. The element is also a type that also needs to be equipped with filter press equipment, & filter material (regular replacement), = 2, and it will be blocked if it is consumed, and it needs to be far away regularly. And 'would have the problem of waste water discharge: it is extremely inconvenient to outline the technology and purpose of the present invention. The present invention is to provide a previously-available & process method system that saves space, resources, and processes. Its main technology and purpose are: one of excellent separation, speed, and true separation. It has a unique circuit connected oxidation ^ ^ fr γμ λμ ^ η MG 7 ^, magnesium oxide pyrolysis tank, = Syria: tank , Absorption tower, oxidation tank, bottom tank, reaction tank, hydroxide storage tank: dagger storage tank, first sedimentation tank, second Shendian tank, with furnace water seal to separate wastewater into magnesium hydroxide solution and Calcium sulfate by-products have the effect of preventing secondary pollution from discharged wastewater. Second, the overall system operation, i automatically circulates, there will be no disturbance of wastewater discharge. Ya'a can save the space and deal with the situation quickly, so that the wastewater treatment of the steam and electricity co-generation equipment can achieve excellent environmental protection effect. In order to allow the Bureau ’s review members and those skilled in this art to
第7頁 508264Page 7 508264
之功效完全瞭解,兹配合實施例圖式及圖號,就本發明之 構成、流程、作用、功效,詳細說明如下: 茲以圖一實施例說明之,係包含··氧化鎂貯槽丨〇、氧 化鎂(MgO )熱解槽11、氲氧化鎂(Mg(〇H)2 )儲槽12、1 收塔13、氧化槽14、底灰攪拌池15、氯化鈣(CaC12 ) 槽1 6、第一沈澱槽24、鍋爐水封丨8、反應槽丨9、氧化: 儲槽20、氧化鈣(Ca〇 )攪拌槽21、氧氫化鈣儲槽“、、’ 氧化鎂緩衝桶23、第二沈澱槽17所構成;其系統曰安 里 處理之方法流程為: 、 氧化錤貯槽1 0 :貯存氧化鎭(M g 〇 ) 解槽1 1 ; 並連通至氧化鎂熱The effect is fully understood, and the structure, process, function and effect of the present invention are described in detail with the illustrations and numbers of the embodiments. The following is an illustration of the first embodiment, which includes a magnesium oxide storage tank. Magnesium oxide (MgO) pyrolysis tank 11, hafnium oxide (Mg (〇H) 2) storage tank 12, 1 collection tower 13, oxidation tank 14, bottom ash mixing tank 15, calcium chloride (CaC12) tank 1, 6, First sedimentation tank 24, boiler water seal 丨 8, reaction tank 丨 9, oxidation: storage tank 20, calcium oxide (CaO) stirring tank 21, calcium oxyhydrogen storage tank "," magnesium oxide buffer tank 23, second The sedimentation tank 17 is formed; the method of the system is described as follows: 、 oxidized oxide storage tank 10: storage of dysprosium oxide (Mg 〇) solution tank 1 1; and communicates with the magnesium oxide heat
氧化鎂熱解槽1 1 拌,並在 或蒸汽, 乳泥,再 化鎂儲槽 將所接受之氧化鎂粉末加水授 撥拌之過程予加入少量之熱水 以使氧化鎭熱解成為氫氧化鎂 經輸送泵浦Μ P予以栗送至氫氧 12 ; 氫氧化鎂儲槽1 2 ·貯存氫氧化錤乳泥並持續予以授拌,並Magnesium oxide pyrolysis tank 1 1 Mix, and in the process of steaming, milking mud, and re-magnesium storage tank, add the received magnesium oxide powder to the water and mix it. Add a small amount of hot water to pyrolyze the tritium oxide into hydroxide. Magnesium is pumped to the oxygen and hydrogen 12 by the pump MP; the magnesium hydroxide storage tank 1 2 stores the mash of mash and continues to be blended, and
配自又輸送栗浦予加注至吸收搭1卩· 吸收塔1 3 :係具有煙氣脫硫作用,煙氣流由下往上斗 吸收塔内之由上層往下喷淋之循接: ^ 以吸收煙氣中之硫氧化物,且悬μ a 令于齊态130,可除去脫硫後之煙氣中 %内部之循環液需加入氫氧化鎂孰、、尸 丄 豕浦ΜΡ送入、吸收反應後之反應物為硫酸Equipped with a pumping pump from Lipu to the absorption 1 卩 · absorption tower 1 3: It has the function of flue gas desulfurization, and the flow of the flue gas flows from the bottom to the top of the absorption tower. The sulfur oxides in the flue gas are suspended in a homogeneous state of 130, which can remove the% of the circulating fluid in the flue gas after desulfurization. Magnesium hydroxide is required to be added, and the corpse pump MP is fed and absorbed. Sulfuric acid
第8頁 508264Page 8 508264
鎮或亞硫酸鱔廢液,並予抽送至氧化槽1 4再處 理; 义 氧化槽14 ··具有攪拌功能,而可增進曝氣、增進氧化作用 ,使殘餘之亞硫酸鎂(MgS03)氧化呈硫酸鎂 水溶液; ' 氯化鈣儲槽16 :儲存氯化鈣CaC12,並配設輪送泵浦評連 通至底灰攪拌池1 5 ; 底灰攪拌池1 5 ·具有攪拌功能,承受氧化槽丨4之3〜5 %硫The sulphuric acid or thorium sulfite waste liquid is pumped to the oxidation tank 14 for further treatment; the oxidation tank 14 has a stirring function, which can increase aeration and oxidation, and oxidize the residual magnesium sulfite (MgS03). Magnesium sulfate aqueous solution; 'Calcium chloride storage tank 16: stores calcium chloride CaC12, and is equipped with a wheel pump to communicate with bottom ash mixing tank 15; bottom ash mixing tank 15 · with stirring function, withstand oxidation tank 丨3 of 4 to 5% sulfur
酸鎂MgS04溶液、及承受氯化鈣儲槽丨6加 入之氯化鈣,而使之化學反應作用,產生 氣化鎂MgC 1 2,再被泵送至第一沈殿槽2 4 ;又,其亦承受第二沈澱槽丨7上層反應物 氯化#5溶液、鋼爐水封1 8之水溶液,而得 再次循環處理呈氯化鎂狀態再又送回第二 沈澱槽1 7 ; 氧化鈣貯槽20及氧化鈣攪拌槽21 :係將氧化鈣Ca〇加水,Magnesium acid MgS04 solution, and calcium chloride added to the calcium chloride storage tank 丨 6, and made it react chemically to produce gasified magnesium MgC 1 2 and then pumped to the first Shendian tank 2 4; It also withstands the second reaction tank 丨 7 upper reactant chlorination # 5 solution, steel furnace water seal 18 aqueous solution, and can be recycled to the magnesium chloride state and sent back to the second precipitation tank 17; calcium oxide storage tank 20 and Calcium oxide stirring tank 21: Add calcium oxide Ca0 to water,
予以授拌均勻,產生水 解反應作用而形成氫氧 化鈣Ca(0H)2乳泥,再 配設輪送泵浦MP輸送至 ^ 氫氧化鈣儲槽2 2 ; 氫氧化鈣儲槽22 :係儲存氫氧化鈣,再配設輸送泵浦Mp輸 送加入反應槽1 9 ; 反應槽19 ·係承受第二沈澱槽17上層含氯化鎂MgC1 2水溶It is mixed evenly to produce a calcium hydroxide Ca (0H) 2 emulsion, which is hydrolyzed, and is equipped with a rotary pump MP to transport to ^ calcium hydroxide storage tank 2 2; calcium hydroxide storage tank 22: Department of storage Calcium hydroxide, equipped with a pump Mp, is added to the reaction tank 19; reaction tank 19 · The second sedimentation tank 17 bears the upper layer containing magnesium chloride MgC1 2 water-soluble
第9頁 508264 五、發明說明(5) 液、及氫氧化鈣儲槽22之氫氧化鈣溶液,使之 混合產生氯化鈣CaCl 2與氫氧化鎂Mg(〇H)2溶液 ’再配設輸送系浦Μ P抽送至第二沈澱槽1 7分 離及再處理; 第一沈澱槽2 4 :係承受反應槽1 9之水溶液,做氯化每及氯 氧化鎮水溶液之沈降分離,上層為氯化約 浴液回至底灰撥掉池1 5反應,再輸送至 第二沈澱槽1 7,下層為氫氧化鎂水溶液則 輸送至氫氧化鎂緩衝桶23後再輸送加入吸 收塔13 ; 氫氧化鎂緩衝桶23 :配設輸送泵浦MP將還原之氫氧化鎮水 溶液,輸送加入吸收塔1 3循環液,俾 再經脫硫吸收,及氧化槽1 4、底灰授 拌池1 5、第二沈殿槽1 7、反應槽1 9、 第一沈澱槽24之循環作用處理; 苐二次沈殿槽1 7 :係承受底灰授拌池1 5之溶液,產生沈凝 作用,並將上層氯化鎂MgC12溶液又導 入反應槽1 9再反應作用,下層之沈殺物 即硫酸鈣CaS04之泥狀物質,即流至麵 爐水封1 8 ; 鍋爐水封1 8 :具有輸送帶1 8 0,其承受第二次沈澱槽丨8之 泥狀物質,而得予加強分離呈水(H20)、硫 酸I弓C a S 0 4灰泥,水呈處於上層,再溢流至 底灰攪拌池1 5,而泥狀物之硫酸鈣灰泥、則Page 9 508264 V. Description of the invention (5) Liquid and calcium hydroxide solution of calcium hydroxide storage tank 22, mixed to produce calcium chloride CaCl 2 and magnesium hydroxide Mg (〇H) 2 solution The pumping system is pumped to the second sedimentation tank 17 for separation and reprocessing; the first sedimentation tank 24 is the aqueous solution that is subjected to the reaction tank 19 for sedimentation and separation of chlorination and chlorine oxidation aqueous solution. The upper layer is chlorine. The caustic solution is returned to the bottom ash and the pool 15 is reacted, and then sent to the second precipitation tank 17; the lower layer is the magnesium hydroxide aqueous solution, which is then transferred to the magnesium hydroxide buffer tank 23 and then transferred to the absorption tower 13; Magnesium buffer bucket 23: equipped with a transport pump MP to transport the reduced hydroxide aqueous solution to the absorption tower for 1 to 3 circulating fluids, which are then desulfurized and absorbed, and the oxidation tank 1 4 and the bottom ash mixing tank 15 5 The second Shendian tank 17, the reaction tank 19, and the first sedimentation tank 24 are circulated. 苐 Second Shendian tank 17: It is a solution that bears the bottom ash mixing tank 15 to produce sedimentation, and the upper layer of magnesium chloride The MgC12 solution was introduced into the reaction tank 19 again for reaction, and the sinker in the lower layer was the clay-like form of calcium sulfate CaS04. Substance, that is, the water seal flowing to the surface furnace 18; Boiler water seal 18: It has a conveyor belt 180, which bears the mud-like substance of the second sedimentation tank 丨 8, and can be strengthened to separate into water (H20), The sulfuric acid I bow C a S 0 4 stucco, the water is in the upper layer, and then overflows to the bottom ash mixing tank 15, and the calcium sulfate stucco of the mud,
第10頁Page 10
藉由上述之構 細節說明如下 本發明係 (一) 多次循 本發明之 ,且吸收塔1 3 以除去水份。 本發明係 底灰攪拌池15 、氯化鎂)先 沈降),後, 化甸(含氧化 2 2 )之作用, 輸送至氫氧化 中、氯化舞者 澱槽1 7,後, 分離氫氧化鎂 爐水封1 8輸送 (二) 零廢水 ^皮輸送帶180輸送至底灰貯槽,#回收利用· 成與迴路系統,本發明之作用、功效,兹再 具有下列之獨特作用及功效·· 環處理廢水中物質’回收氫氧化鎂溶液: =排出〇,係呈「唯_」之吸收和 上層設有除霧器130,使煙氣流通過除霧器 故,所排放之煙氣,必達環保標準。The above-mentioned structure is explained in detail as follows. The present invention is (a) the invention is repeated multiple times, and the absorption tower 13 is used to remove water. In the present invention, the bottom ash stirring tank 15 (magnesium chloride) is first settled), and then, the role of Huadian (containing oxidation 2 2) is transferred to the hydroxide, chloride dancer bowl 17, and then, the magnesium hydroxide furnace is separated. Water seal 18 (2) Zero waste water ^ skin conveyor belt 180 is conveyed to the bottom ash storage tank, #recycling, recycling and loop system, the function and effect of the present invention, and it has the following unique functions and effects ... Substances in wastewater 'recovery of magnesium hydroxide solution: = Discharged 0, which is "only" absorption and the upper layer is equipped with a mist eliminator 130, so that the flue gas flow passes through the mist eliminator, so the emitted smoke must meet environmental protection standards.
呈「連續循環」處理,乃是:經氧化槽14、 士第:沈澱槽17 ’讓底部之泥狀⑯(硫 由鍋爐水封18沈降排除之(亦即,先做初牛 車乂不易沈殿之水溶液,再經反應槽^ 9、 約貯槽20、氧化樣"曹21、氫氧化 再經第一沈澱槽24,後又分離呈氫氧化鎂 鎮缓衝桶2 3及回收輪送加入吸收塔丨3循产 回收輸送至底灰攪拌池丨5,再輸^至第=& 又再如上述之循環作用,如此周而復始了 = 及氯化鈣水溶液回收再利用,而泥狀物由^ 帶1 8 0輸送至底灰貯槽再利用處理。 1It is treated in a "continuous cycle", which is: through the oxidation tank 14, and the first: the sedimentation tank 17 'to allow the bottom of the mud-like ⑯ (sulfur is settled by the boiler water seal 18 to exclude (that is, it is not easy to make the first ox cart 乂 Shen Dianzhi The aqueous solution is then passed through the reaction tank ^ 9, about storage tank 20, oxidation sample "Cao 21", the hydroxide is passed through the first precipitation tank 24, and then separated into the magnesium hydroxide town buffer bucket 2 3 and the recycling wheel is added to the absorption tower丨 3 Recycling and transporting to bottom ash mixing tank 丨 5, and then ^ to the ^ = and again the above-mentioned cycle action, so again and again = and calcium chloride aqueous solution recovery and reuse, and the sludge by ^ belt 1 80 is transported to the bottom ash storage tank for reuse. 1
排放: #本發明可謂是「零排放」,因:只呈吸收塔丨3上方 ^ ^氣条發’而此水蒸氣係清潔之水,另,即是由鍋憐水 封18之輸送帶180輸送出泥狀物,再回收處理(此非本…安 申請標的,諒不予冗載),故,無大量之廢氣、廢水排木放Discharge: #The present invention can be described as "zero emissions", because: only above the absorption tower 丨 3 ^ ^ air strips, and this water vapor is clean water, and the conveyor belt 180 is sealed by the pot water 18 The mud is conveyed out, and then recycled (this is not the subject of the safety application, please do not overload), so there is no large amount of waste gas and waste water.
508264 問題 系統 在小場地中即可使用,呈一種 不會有廢水排放至外處之困擾 ^發明將廢水所含之硫酸鎂還原成氫氧化鎂,再呈 「水H20」、「硫酸鈣CaS04」、「氯化鎂MgC;l2」 ,回收之化學反應為: 再生回收」之處 理 因、’,廢水本身即含有硫化物、及在氧化槽1 4與底灰 攪拌池1 5中,有加入3〜5 %硫酸鎂MgS〇4、及攪拌 曝氣加強氧化,故,會有下列之反應: 氫氧化鎂吸收S〇2主要反應如下:508264 The problem system can be used in a small site, and there is no problem that waste water is discharged to the outside. ^ Invention of reducing magnesium sulfate contained in waste water to magnesium hydroxide, and then showing "water H20" and "calcium sulfate CaS04" "" Magnesium chloride MgC; l2 "", the chemical reaction of the recovery is: "Regeneration and recovery", "The wastewater itself contains sulfide, and in the oxidation tank 14 and the bottom ash mixing tank 15, there are 3 ~ 5 % Magnesium sulfate MgS04, and agitated aeration to enhance oxidation, so the following reactions will occur: The main reaction of magnesium hydroxide absorption S02 is as follows:
Mg(0H)2 +S02->MgS03 +2H20Mg (0H) 2 + S02- > MgS03 + 2H20
MgS03 +S02 +H20->Mg(HS03)2 通常煙氣中含有3〜8 %之〇 2,經由自然氧化使吸收 液中之MgS03與Mg(HS03)2 (或經由強制曝氣氧化) 部份或絕大部份氧化成MgS04,其反應式如以下兩 反應,MgS03 + S02 + H20- > Mg (HS03) 2 Generally, the flue gas contains 3 ~ 8% 〇2. MgS03 and Mg (HS03) 2 in the absorption liquid are oxidized by natural oxidation (or oxidized by forced aeration). Or most of them are oxidized to MgS04, the reaction formula is as follows:
MgS03+l/2 02 + 7H20—MgS04 · 7H20 Mg(HS03) 2 +02 + 7H20-^MgS04 · 7H20+H2S04MgS03 + l / 2 02 + 7H20—MgS04 · 7H20 Mg (HS03) 2 +02 + 7H20- ^ MgS04 · 7H20 + H2S04
2.又,因有由氧化鈣CaO經氧化鈣攪拌槽21之水及攪 拌(水解作用),產生氫氧化鈣Ca(0H)2乳泥,亦 即,有加入氫氧化鈣,故,會有下列之反應: MgS04 +Ca(0H)2 + 2H20->Mg( OH) 2 +CaS04 · 2H20 MgC12 + Ca(0H)2—>Mg(0H)2 + CaC12 H2S04+Ca(0H)2—CaS04 · 2H20 MgS04 +CaC 1 2 +2H20—MgC12 +CaS04 · 2H202. Also, because calcium oxide CaO passes through the water and stirring (hydrolysis) of the calcium oxide stirring tank 21, calcium hydroxide Ca (0H) 2 emulsion is produced, that is, calcium hydroxide is added, so there will be The following reactions: MgS04 + Ca (0H) 2 + 2H20- > Mg (OH) 2 + CaS04 · 2H20 MgC12 + Ca (0H) 2— > Mg (0H) 2 + CaC12 H2S04 + Ca (0H) 2— CaS04 · 2H20 MgS04 + CaC 1 2 + 2H20—MgC12 + CaS04 · 2H20
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第12頁 508264 五、發明說明(8) 亦即’會有上述之「交互反應」’因而可將氫氧化鎂 Mg(0H)2再生回收,亚,產生石貧(CaS04 . 2H2〇)之副產 物。 (四)可理::離ir月含有化學物質之灰泥、廢水 廢水耕放之功效,具有省資源^ /到零 環保之功效。 名成本、癌人工、 綜上所述,本發明之系絲讲斗从「 之領域,確實是前所未有之舍又" ;汽電共生設備」 實具有極佳之產業實用價值丄而所達成之功效,亦確 賜准專利,實感德便。 ’誠符合發明專利要旨,懇請 圖式簡單說明: 圖 圖一,係本發明系統流程示立 圖號說明: $ @ 10氧化鎂貯槽 11氧化鎂熱解槽 12 氫氧化鎂儲槽 13 吸收塔 1 3 0除霧器 14氧化槽 1 5底灰授摔池 1 6氯化转儲槽 17第二次沈澱槽 1 8 鍊;爐水封 180輸送帶 19反應槽 20氧化鈣貯槽 21氧化鈣攪拌槽 2 2氫氧化|弓儲槽 2 3 氫氧化鎂緩衝桶 24 第一次沈澱槽 MP輸送泵浦Page 12 508264 V. Description of the invention (8) That is, “there will be the“ interaction ”mentioned above, so magnesium hydroxide Mg (0H) 2 can be regenerated and recovered, and vice-versa will produce stone lean (CaS04. 2H2〇). product. (4) Reasonable: The stucco and waste water containing chemical substances from the month of irrigation has the effect of cultivating waste water, which has the effect of saving resources ^ / to zero and environmental protection. In the above, the cost of cancer, labor, and artificial intelligence. In summary, the system of the present invention achieves what has been achieved from the "field, which is indeed an unprecedented house"; "steam-electricity symbiosis equipment". Efficacy is also granted a quasi-patent, which is a real virtue. 'It is in line with the gist of the invention patent, and I kindly ask for a simple explanation of the figure: Figure 1 is a drawing showing the system flow chart of the present invention: $ @ 10Magnesium oxide storage tank 11 Magnesium oxide pyrolysis tank 12 Magnesium hydroxide storage tank 13 Absorption tower 1 3 0 mist eliminator 14 oxidation tank 1 5 bottom ash transfer tank 1 6 chlorination dump tank 17 second sedimentation tank 1 8 chain; furnace water seal 180 conveyor belt 19 reaction tank 20 calcium oxide storage tank 21 calcium oxide stirring tank 2 2 Hydroxide | Bow storage tank 2 3 Magnesium hydroxide buffer bucket 24 First MP precipitation pump
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TW90132641A TW508264B (en) | 2001-12-25 | 2001-12-25 | Discharge and regeneration system for cogeneration desulfurization device with zero discharge |
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Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1318318C (en) * | 2003-01-27 | 2007-05-30 | 荣成纸业股份有限公司 | Treatment system for waste water from exhaust gas desulfurization in gas-electricity generating device |
CN102553418A (en) * | 2011-11-18 | 2012-07-11 | 浙江荣成纸业有限公司 | Zero-emission magnesium hydroxide regeneration and recovery system of steam-electric desulfurization equipment |
-
2001
- 2001-12-25 TW TW90132641A patent/TW508264B/en not_active IP Right Cessation
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1318318C (en) * | 2003-01-27 | 2007-05-30 | 荣成纸业股份有限公司 | Treatment system for waste water from exhaust gas desulfurization in gas-electricity generating device |
CN102553418A (en) * | 2011-11-18 | 2012-07-11 | 浙江荣成纸业有限公司 | Zero-emission magnesium hydroxide regeneration and recovery system of steam-electric desulfurization equipment |
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