201104062 六、發明說明： 【發明所屬之技術領域】 本發明是一種應用於發電機或動態不斷電系統之脫硝級 智慧型全功能柴油引擎廢氣處理系統，特別指應用於處理 發電機或動態不斷電系統所排出的引擎廢氣之脫硝級智慧 型全功能柴油引擎廢氣處理系統。 【先前技術】 應用於發電機或動態不斷電系統之柴油引擎廢氣處理系 統，是業界已知之技術’通常以下列兩種方式處理廢氣： (1) 利用黑煙過濾器處理固態的微細碳粒子（particuiate) (2) 利用氧化型觸媒轉化器處理氣態的碳氫化合物 (Hydrocarbons)及一氧化碳（Carb〇n M〇n〇xide)。以下為習 知柴油引擎廢氣處理系統：台灣專利公告第373688號揭露 一種改良型排氣管，其是以—倒】形管接於排氣管來形成 兩出口端’其中-出口端連接—濾煙器以濾除粒狀污染 物；台灣專利公告第M251021號揭露一種附微波之引擎排 氣渡心，尤指-種可藉微波之輻射直接對積置於渡心通道 内之微粒子（積碳）加熱燃燒，使其提早觸媒或擔體之工作 及反應之溫度時間，有效提高其起燃之溫度；台灣專利公 告第M299775號揭露-種柴油引擎排氣淨化裝置，一過滤 元件係橫設於該本體内部中段， 可過濾由排氣管導入廢氣201104062 VI. Description of the Invention: [Technical Field of the Invention] The present invention relates to a denitration-grade intelligent full-function diesel engine exhaust gas treatment system applied to a generator or a dynamic uninterruptible power system, particularly for processing a generator or a dynamic Denitration-grade intelligent full-featured diesel engine exhaust gas treatment system for engine exhaust gas discharged from the uninterruptible power system. [Prior Art] A diesel engine exhaust gas treatment system applied to a generator or a dynamic uninterruptible power system is a technique known in the art. The exhaust gas is usually treated in the following two ways: (1) Treatment of solid fine carbon particles by a black smoke filter (particuiate) (2) Treatment of gaseous hydrocarbons (hydrocarbons) and carbon monoxide (Carb〇n M〇n〇xide) using an oxidizing catalyst converter. The following is a conventional diesel engine exhaust gas treatment system: Taiwan Patent Publication No. 373688 discloses an improved exhaust pipe which is connected to an exhaust pipe by an inverted pipe to form two outlet ends 'where-outlet end connection-filtering The cigarette smoker filters out particulate pollutants; Taiwan Patent Publication No. M251021 discloses a microwave exhaust engine, especially a kind of microparticles (carbon deposits) that can be directly deposited in the center channel by microwave radiation. Heating and burning, so that the temperature of the working and reaction of the catalyst or the carrier is increased, and the temperature of the light-off is effectively increased; Taiwan Patent Publication No. M299775 discloses a diesel engine exhaust purification device, and a filter element is arranged horizontally. In the middle part of the body, the exhaust gas can be filtered by the exhaust pipe
140426.doc 201104062 揭露一種淨煙器之後喷系統，可加裝於各種舊形柴油車 上，主要係由一柴油汽化裝置及一濾煙器所組成，其中， 柴油汽化裝置主要係將柴油加以汽化，而濾煙器主要在藉 由自燃及過渡而遽除一氧化碳、碳氯化合物、微顆粒、黑 煙及臭氣；台灣專利公告第577482號揭露一種排煙淨化改 • 1裝置’將—升溫控制單元之加熱器，作為觸媒轉化器因 引擎排氣之溫度不足，加熱補償瞬間溫升之不足；以及台 • 灣專利公告第M317493號揭露一種柴油引擎排煙改善污染 後處理輔助加熱器結構，利用氣體導入排煙管的同時，藉 由壓力差將燃油抽出’經线霧化點火後，與引擎所排放 之未完全燃燒之廢氣再次燃燒所產生的熱能，將排煙淨化 益濾芯所補捉之碳粒子加熱再次燃燒，提昇淨化器的除煙 除臭除毒之功能。 此外，關於處理毒性的氮氧化物（Ν〇χ)部份，業界已知 之技術包含以選擇性觸媒還原法（Selective Catalytic • 簡稱為SCR)，來處理氮氧化物⑽X)，當氮氧化 物（NOx)通過脫硝觸媒時，利用氨氣作為選擇性觸媒還原 法所使用的還原劑’將氮氧化物(NOx)轉化成氮氣和水。 * 以下為％知處理毒性的氮氧化物的技術：美國專利公告號 5,489,420揭露一種藉由於高溫下將還原劑添加至氮氧化物 以移除氮氧化物的技術，其中使用氨氣於95(rc或更高的 同，皿下，將氮氧化物移除；，美國專利公告號5,443,8〇5與 5,536,482揭露一種藉由在90〇t至12〇〇<t下，將聚合物加 入氨氣中來移除氮氧化物的方法；台灣專利公告第 140426.doc 201104062 M271135號揭露一種選擇性觸媒還原脫硝系統，係利用還 原法，以注入氨氣（AmmoniaNH3)當還原劑，當氮氧化物 以及氨氣流經觸媒床，即將氮氧化物還原成氮氣（Nj及水 (Ηβ);以及台灣專利公告第j 2485〇4號揭露一種加氨子系 統，包括氨蒸氣源、設置於進口管道中之氨注入栅網、與 於氨蒸氣源與氨注入栅網間，提供流體通道之氨蒸氣管以 及設置於氨蒸氣管中之節流閥，混合氨蒸氣之步驟還包括 藉由加氨控制器調節節流閥來控制加氨氣之速率。 矣又而口黑煙過;慮器之目的在過渡固態的微細碳粒子 (Particulate)，通常使用的是多孔性陶瓷濾材其出入口兩 端呈現蜂巢狀。因此當黑煙廢氣經由過濾器入口端進入蜂 巢式通道後，因通道出口端被封閉，而無法穿過，碳粒子 (Particulate)被蜂巢式濾材所捕捉，進而達到過濾黑煙廢氣 之效果。雖然黑煙過濾器確實能夠達成特定功效，但事實 上，單獨以此類傳綠過濾器處理引擎廢氣仍有許多缺點： ⑴黑煙過據器只能過濾黑煙，而且渡材必須經常停機再 生清理，以免堵塞，所以無法配合引擎長時間運轉。（？) 蜂巢壁流式ms有很高的壓降，因此所裝設的傳統型 「黑煙過遽器」數量亦非常龐大，系統設置f用約為使用 氧化型觸媒轉化器的5至丨5倍，價格非常昂貴。 氧化型觸媒轉化器（Diesel 〇xidati〇n Cataiyst)的目的在 處理氣態蚊氫化合物（Hydr〇carb〇ns)與一氧化碳（Carb〇n M〇noxlde)。利用氧化型觸媒披覆在陶泛或金屬母材表 面用來降低氣態的碳氫化合物（Hydrocarbons)與一氧化 140426.doc 201104062 碳（Carbon M〇n〇xide)燃燒溫度後，再利用引擎排氣溫 度，來將廢氣中的氣態碳氫化合物（Hydr〇carb〇ns)與一氧 化碳（Carbon M〇noxide)轉化成水與二氧化碳。然而，單 獨只以氧化型觸媒轉化器（Diesel 〇xidati〇n㈤㈣）處理 引擎廢氣亦有（1)無法處理引擎瞬間起動時所產生大量黑 煙（2)無法處理低引擎負載運轉；低排氣溫度（<25〇°c ) 時，所產生的氣態碳氫化合物（Hydr〇carb_)與一氧化碳 (Carbon Monoxide)等缺點。 有關以選擇性觸媒還原法（SCR)，來處理毒性的氮氧化 物（N〇x)部份，因業界已知之柴油引擎廢氣處理技術並不 成熟，且受限於變動的引擎負載與變動的氮氧化物（Ν〇χ) 排放濃度；尤其在引擎無載運轉時，極低的排氣溫度（低 於25〇°C-3GGt)時，選擇性觸媒還原法將無法進行。選擇 以氨氣（八職心題3)當還原_，因氨氣屬於毒性化學 物質，在排氣溫度極低時，因無法與氮氧化物（Ν〇χ)充分 有效的進行還原反應’氨氣有溢出（Ammonia Slip)的危 險。 雖然風氣應用在選擇性觸媒還原法（SCR)進行脫硝 (DeNOx)時’是一個非常良好的還原劑，惟其蒸汽麼為 7.76 atm ’其彿點為_33 4〇c，亦即在常溫、常壓下，以氣 體方式呈現’屬於強烈毒性、腐韻性的化學氣體。在高溫 下’會分解成為可燃性氫氣與毒性氣體，火★昜中儲存氨氣 ’亦會產生破裂與爆炸的危害。因此，氛氣儲 存於至内時’安全性更是必須加以慎重的考量。基於上述 140426.doc 201104062 種種限制與氨氣儲存使用上’安全性的考量，目前業界已 知之技術’針對發電機或動態不斷電系統所排出的柴油引 擎廢氣中所含毒性氮氧化物（N〇x)的部份，尚無經濟、有 效的處理技術。 另外選擇性觸媒還原法（SCR)，使用氨氣作為還原劑， 為業界已知之技術，基本上分為「液態氨」及「尿素水溶 液」兩大類《如下所述，無論是液態氨或尿素水溶液，在 應用上仍有諸多缺點與不便： (一）液態氨（Liquefied Ammonia)(NH3) 液態氨不易儲存，須以8 kg/cm2以上的壓力，將液態氨 儲存在壓力容器内，使用時再以汽化方式，先將液態氨汽 化後，再將氨氣直接喷入選擇性觸媒還原法（SCR)脫硝設 備中，其缺點為須以壓力容器儲存液態氨，且儲存液態氨 的壓力容器’放在室㈣㈣空間，若氨氣發线漏時， 氨氣會與空氣混合，有發生爆炸的危險。 (二）尿素水溶液（AqUeous Urea soluti〇nXc〇NH2)2 尿素在常溫、常壓下’呈現無色結晶固體形狀，可以溶 於水。傳統作法是將尿素水溶液中所含尿素濃度調整在 32.5%左右，作為選擇性觸媒還原法（scr)處理氮氧化物 ⑽X)的還原齊卜當排氣溫度高於16〇t日夺，噴入選擇性觸 •媒還原法SCR脫硝設備中的尿素水溶液，會在高溫下先行 分解成為氨氣與二氧化碳，纟中氨氣再與I氧化物 反應，將其轉變為氮氣與水後，再排放至大氣。 尿素的缺點包括：（1)尿音、为、* β Λ J尿素水/合液須先行.分解成為氨氣 140426.doc 201104062 再進行脫硝反應（DeNOx) ’屬於間接式氨氣注入法，因此 由尿素轉換為氨氣的反應速度與效率，比較難以控制；（2) 在注入喷嘴部份’經常會有固體雜質產生，造成堆積與喷 嘴堵塞，進而影響喷嘴喷霧的效果；（3)在常溫環境下 (35°C-60°C) ’會有部份尿素水溶液分解成為氨氣與二氧化 碳’容易造成氨氣外洩的危害；（4)在低溫環境下（<_ 11°C )’尿素水溶液會產生凝結現象；以及（5)與液態氨比 較’須有相當約2.5_3倍容積空間來儲存，並且脫确的效 果並無法與液態氨相比。 綜上，相關習知技術不外乎單獨依賴黑煙過濾器來過濾 固態的微細碳粒子（Particulate)、或是單獨依賴氧化型觸媒 轉化器（Diesel Oxidation Catalyst)來處理氣態的碳氫化合 物（Hydrocarbons)與一氧化碳（Carbon Monoxide)之混合 物、或是以黑煙過濾器披覆氧化型觸媒來同時處理固態的 微細碳粒子（Particulate)及碳氫化合物（Hydrocarbons)、一 氧化碳（Carbon Monoxide)、或是依賴儲存於高壓壓力容器 内的液態氨、或是利用需要大容量儲存空間、及諸多處理 技術限制的尿素水溶液，以選擇性觸媒還原法（SCR)脫;6肖 設備處理氣氧化物（NOx)。 不論是使用黑煙過濾器（含觸媒披覆）、或是使用氧化型 觸媒轉化器、或是使用以液態氨或尿素水溶液為還原劑的 選擇性觸媒還原法（SCR)脫硝設備，皆無法同時經濟、安 全、有效處理含有毒性的氮氧化物（NOx)、氣態的碳氫化 合物（Hydrocarbons)、一 氧化碳（Carbon Monoxide)與固態 140426.doc 201104062 的微細碳粒子（partculate)之引擎廢氣。因此，實有必要提 供一種可自動偵測廢氣污染狀況，以彈性、經濟、有效地 運用碳化矽除煙陣列、固態無機鹽類氨儲存器、選擇性還 原觸媒陣列及氧化型觸媒除臭陣列，以不同於上述常見的 引擎廢氣處理習知技術，全面淨化所有引擎廢氣中的污染 物質’包括毒性的氮氧化物（Ν0χ)、氣態的碳氫化合物 (y ocarbons)、一 氧化碳（Carb〇n M〇n〇xide)與固態的微 細碳粒子（Partieulate)，專門應用於發電機或動態不斷電系 統之柴油引擎廢氣處理系統。 【發明内容】 本發明之目的’在提供一種可克服前述習知技術缺點， 應用於發電機或動態不斷電系統，可自動偵測廢氣污染狀 兄以彈性、經濟、有效地運用碳化石夕除煙陣列、固·離益 機鹽類氛儲存器、選擇性還原觸媒陣列及氧化型觸媒：： 陣列之脫硝級智慧型全功能柴油引擎廢氣處理系統。本發 明針對傳統黑煙過滤器及氧化型觸媒轉化器之缺點加以整 合改良，並以先進的氨氣儲存供應區結合選擇 陣列(SCR)，以達全功能 ？觸媒 … 取佳曆孔處理效果。本發明所 捕存供應區包括：固態無㈣類氨㈣器 140426.doc 201104062 ’、2004年口 4電力設施空氣污染物排放標準。 本發月係關於_包括一廢氣流動區之脫硝級智慧型全 功月b木油引擎廢氣處理系統，用來處理引擎所排出之引擎 =氣。該廢氣流動區包括：一用以供引擎廢氣導入廢氣流 動區之中間聯絡管、5 ,丨、 « , 至乂 一氧化型觸媒除臭陣列、至少一 «性還原觸媒陣列、至少—碳化錯煙陣列及—排氣主 e «亥至v t化型觸媒除臭陣列與中間聯絡管直接或間 接相通’以處理來自中間聯絡管之碳氫化合物 (Hydrocarbons)或一氧化碳（Carb〇n施應叫廢氣。該至 少-選擇性還原觸媒陣列與中間聯絡管直接或間接相通， 乂處理來自中間聯絡官之氮氧化物（Ν〇χ)廢氣。該至少一 碳化石夕除煙陣列與中間聯絡管直接或間接相通，以過渡來 自中間聯絡管含有固態微細碳粒子的廢氣。該排氣主管盘 該碳化石夕除煙陣列間接或直接相通，以將經由碳化石夕除煙 陣列過滤後之廢氣排放至大氣。該廢氣流動區界定出第一 廢氣處理路徑及一第二廢氣處理路徑。該第-廢氣處理路 ,及第一廢乳處理路控均延伸於該中間聯絡管及該排氣主 管之間；且在該第-廢氣處理路徑中，廢氣先後通過該中 間聯絡官、該至少一碳化石夕除煙陣列、該至少一氧化型觸 媒除臭陣列、該至少一選擇性還原觸媒陣列，及該排氣主 管’而在該第二廢氣處理路徑中，廢氣先後通過該中間聯 絡e、邊至少一氧化型觸媒除臭陣列、該至少一選擇性還 原觸媒陣列、s玄消音器及該排氣主管。該廢氣流動區可在 其適當位置處藉一排氣偵測裴置偵測一引擎廢氣資料，因 140426.doc -11- 201104062 此田該引擎廢氣經由中間聯絡管進入該脫硝級智慧型全功 能柴油引擎氣處理系統後，該脫石肖級智慧型全功能柴油？ί 擎廢氣處理系統可利用一微電腦控制器對該引擎廢氣資料 做/出最佳判斷，以決定將引擎廢氣導引通過第一廢氣處理 路從或第二廢氣處理路徑處理後，再排放至大氣。 根據本發明，排氣谓測裝置設於該等廢氣處王里路徑中， 以全方位地連續偵測引擎所排出之廢氣排氣資料，如溫 又壓力仙量、不透光率、碳氫化合物、一氧化碳、硫 氧化物、氮氧化物等。微電腦控制器再根據排氣資料判斷 引擎廢氣污染程度，下達指令選擇適當的廢氣處理路徑， 以達最佳處理效果’使引擎廢氣的黑煙顆粒、碳氫化合 物、氮氧化物及-氧化碳，經過碳化石夕除煙陣列及氧化型 觸媒除臭陣列及選擇性還原觸媒陣列處理。 此外，本發明進一步建議該碳化石夕除煙陣列採用自動再 生之加熱型黑煙過濾器，該氧化型觸媒除臭陣列採用低溫 型觸媒轉化器’並以固態無機鹽類氨錯存器取代傳統的液 態氧、尿素水溶液等氨氣儲存供應方式。加熱型黑煙過遽 益之優點在於高效率處理黑煙、且遽材可自動再生；而低 溫觸媒轉化器之優點在於購置成本低廉、零操作費用、可 在低排氣溫度τ，處理碳氫化合物、—氧化碳及部份里 煙、引擎可以連續運轉’不須要停機。固態無機鹽類氨儲 存器’具有在常溫常壓下’能夠安全無害的儲存供應高純 度氨氣（AmmoniaNH3)以及只雲至_托, 、某要極小室内儲存空間的優 點。以上三種裝置經由本發明之系統整合後，可獲得一不 140426.doc 12· 201104062 可預期之功效。 【實施方式】 圖1所示為本發明之水平對骚 ^ - -置結構之實施例，該圖 所錢石肖級智慧型全功能柴 妊.丄- 丨羊曆乳處理系統1大致包 祜.—由70件編號為10，20，3 150 ^ 40，50，6〇，7〇，8〇， 15〇 #構件組成之廢氣流動區、— 由兀件編號為160， ，“24構件組成之氨氣 1ηπ η 予1/、應£、—微電腦控制器 、及一連接於廢氣流動區、 -,.Μ , Λ 乳氣储存供應區及微電腦 控制βίοο之間之排氣偵測裝置u〇e 廢氣流動區如上所述，較佳句. 丨、一 A 罕乂佳I括.—中間聯絡管10、至 >一:集管20、至少一氧化型觸媒除臭陣列3〇、至少一中 二” 4〇、至少-碳化矽除煙陣列50、至少一上集管6〇、 列^(Γ。主官7〇、一消音器8〇、及至少一選擇性還原觸媒陣 中間聯絡管1〇具有-入口端IL，其連接至引擎排氣口以 ^引擎排出之未處理廢氣。該至少-下集管20使中間 聯絡官1〇與該至少一氧化型觸媒除臭陣列30、及至少一選 擇杜還原觸媒陣列150相連通。該至少-中間集管4〇使中 間％絡管1G與該至少-碳化㈣煙陣列5G相連通。藉此， '^間聯絡官10可與該至少一氧化型觸媒除臭陣列30、及至 、、、擇丨生還原觸媒陣列15 0或至少一碳化發除煙陣列5 〇 溝通。氧化型觸媒除臭陣列30、及至少一選擇性還原觸媒 陣列150與碳化矽除煙陣列50之間可透過中間集管40相互 溝通。 H0426.doc -13- 201104062 每個氧化型觸媒除臭陣列30 ’較佳由至少一個低溫型觸 媒轉化器所組成，在處理引擎低負載、低排氣溫度所產生 的一氧化碳及碳氫化合物之廢氣時，可得最理想之處理功 效。每個碳化矽除煙陣列50，較佳由至少一個加熱型黑煙 過濾器所組成，在高效率過濾黑煙、且濾材可自動再生， 可得最理想之處理功效。 氨氣儲存供應區，較佳由至少一個固態無機鹽類氨儲存 2 160'至少一氨氣定量控制閥161、至少一氨氣產生加熱 器1 62所組成。氣氣儲存供應區在常溫常麗下，可以安全 無害的方式，將高純度的氨氣（Amm〇ni (NOx) ’可最得理想之處理功效。 每組氧化型觸媒除臭陣列職佳包括⑴請低溫型觸 媒轉化器，而氨氣儲存供應區’較佳包括個固態無 機鹽類氨儲存器16〇、12。個氨氣定量控制閥ΐ6ι、以及夏 至2〇個氨氣產生加熱器162。每組碳化石夕除煙陣列5〇、較 佳包括1至20個加熱型黑煙過濾器，而每組選擇性還原觸 媒陣列150、較佳包括！至2()個脫③觸媒轉化器⑴e職 Cata㈣。如圖!所示’在本較佳實施例中，才冓組脫硝級 智慧型全功能柴油料廢氣處理系統1時，係以對稱方式 -〆置氧化觸媒除臭陣列3G、固態無機鹽類氨儲存器 16 〇、氨氣定量控制問m> 女， 句1乳虱產生加熱器162、選擇性 還原觸媒陣列150及碳化矽除煙陣列5〇。 至^上集管6〇使至少一碳化石夕除煙陣列50與排氣主管 I40426.doc 201104062 70相連通，如此經由碳化矽除煙陣列5〇之處理過之淨化氣 體可流通至排氣主管70。消音器8〇之—端透過中間聯狄管 及中間集管40與該至少一氧化型觸媒除臭陣列3〇、選擇 性還原觸媒陣列150溝通，並可提供消音功能。 尤特別的是，如圖2所示，廢氣流動區界定出—第一廢 氣處理路徑A及一第二廢氣處理路徑6，以處理不同污毕 减之廢氣。該第-廢氣處理路徑A及第二廢氣處理路: 鲁 B均延伸於該中間聯絡fl。及該排氣主管7〇之間。如圖以 圖2所示，第-廢氣處理路徑Α，通過至少—碳化㈣㈣ 列5〇、至少一氧化型觸媒除臭陣列3〇與至少一選擇性還原 觸媒陣列150。該第二廢氣處理路徑Β則通過至少一氧化型 觸媒除臭陣列30與至少一選擇性還原觸媒陣列⑼。當引 擎廢氣自中間聯絡管10進入脫確級智慧型全功能柴油引擎 廢氣處理系統增，微電腦控制器⑽可根據引擎廢氣污染 程度，來選擇較佳之廢氣處理路徑，即第一廢氣處理路徑 • Α或第二廢氣處理路徑Β ’以進行最佳廢氣處理後，再排 放至大氣。，經實驗證日月，處理後的引擎錢，能夠符合 2_年中國非道路移動機械用柴油機排氣污染物排放限值 (中國二階段）、2015年歐洲EUR0 4環保四期、2Gu年美國 耵以4環保四期非公路柴油引擎排放標準與2004年台灣電 力設施空氣污染物排放標準。 此外’脫石肖級智慧型全功能柴油引擎廢氣處理系統m 一步包括—安裝於中間聯絡管财排氣主管7G之間適當位 置處之路徑選擇控制閥90。該路徑選擇控制閥90受該微電 140426.doc 15 201104062 腦控制器⑽控制，自動選擇第—廢氣處理路徑A或第二廢 氣處理路徑B ’以選擇最佳方式來處理引擎廢氣。 在脫硝級智慧型全功能柴油引擎廢氣處理系統1安排之 第一廢氣處理路徑入中，廢氣先後通過中間聯絡管丨〇、下 集管20、碳化矽除煙陣列5〇、氧化型觸媒除臭陣列3〇與選 擇性還原觸媒陣列150、及排氣主管7〇。在第二廢氣處理 路徑B中，廢氣先後通過該中間聯絡管1〇、氧化型觸媒除 臭陣列30、選擇性還原觸媒陣列15〇、消音器⑽、及排氣 主管碳化矽除煙陣列5〇，較佳為至少—個加熱型黑煙 過濾器。氧化型觸媒除臭陣列3〇，較佳為至少一個低溫型 觸媒轉化器《選擇性還原觸媒陣列15〇，較佳為至少一脫 硝觸媒轉化器（De NOx Catalyst)。為達到最佳之廢氣處理 效果，氨氣儲存供應區，較佳由至少一固態無機鹽類氨儲 存器160、至少一氨氣定量控制閥161及至少一氨氣產生加 熱器16 2所組成。 排氣偵測裝置11 〇設於該中間聯絡管i 〇，以全方位地連 續偵測進入第一廢氣處理路徑、第二廢氣處理路徑前之引 擎排氣資料’諸如溫度、壓力、流量、不透光率、碳氫化 合物、一氧化碳、硫氧化物、氮氧化物等。 兹就排氣偵測裝置110如何偵測廢氣排氣資料，提供給 微電腦控制器100選擇適當之廢氣處理路徑，例舉說明如 後. 1 ·根據本發明之較佳實施例，當排氣偵測裝置i 10，測 付排载*溫度超過2 5 0 C時，脫硝級智慧型全功能柴油引擎 140426.doc -16 - 201104062 廢氣處理线丨會選擇第二廢氣處理路徑B，亦即純通過 中間聯絡管H)、氧化型觸媒除臭陣3G、選擇性還原觸媒陣 列150、消音器80、及排氣主管7〇，而後將廢氣排放至大 氣。若排氣偵測裝置110，測得排氣溫度低於謂力時，脫 确級智慧型全功能柴油引擎廢氣處理系^會選擇第一廢 氣處理路徑A，亦即先後通過中間聯絡管1〇、下集管2〇、 碳化矽除煙陣列50,氧化型觸媒除臭陣列3〇、選擇性還原 觸媒陣列，及排氣主管7G，而後將處理後的廢氣排放 至大氣。 2.根據本發明之較佳實施例’當排氣偵測裝置ιι〇，測 得排氣系統壓力超過引擎最大容許排氣壓力(― Engine An〇Wable Back p簡ure)時，脫破級智慧型全功能 柴油引擎廢氣處理系m會選擇第二廢氣處理路徑B，亦即 先後通過中間聯絡管10、氧化型觸媒除臭陣列30、選擇性 還原觸媒陣列150、消音器8〇、及排氣主管7〇,而後將處 理後的廢氣排放至大氣。當排氣偵測裝置u〇，測得排氣 系統壓力低於引擎最大容許排氣壓力時，脫石肖級智慧型全 功能柴油引擎廢氣處理系⑹會選擇第_廢氣處理路徑A， 亦即先後通過中間聯絡管10、下集管2〇、碳化石夕除煙陣列 5〇,氧化型觸媒除臭陣列3〇、選擇性還原觸媒陣歹⑽' 排氣主管70，而後將處理後的廢氣排放至大氣。 3.根據本發明之較佳實施例，當排氣制裝置⑽，測 得不透光率超過聰時’脫蹲級智慧型全功能柴油引擎廢 乳處理系統1會選擇第—廢氣處理路徑A，㈣先後通過中 H0426.doc 201104062 間聯絡官10、下集管20、碳化矽除煙陣列5〇，氧化型觸媒 除臭陣列3〇、選擇性還原觸媒陣列150、及排氣主管7〇, 而後將處理後的廢氣排至大氣。而若排氣㈣裝置ιι〇， 測得不透光率低於20%時’脫硝級智慧型全功能柴油引擎 廢氣處理系統1會選擇第二廢氣處理路徑B，亦即先後通過 中間聯絡管10、氧化型觸媒除臭陣列3〇、選擇性還原觸媒 陣列150、>肖音器8G、及排氣主管7()，而後將處理後的廢 氣排至大氣》 4. 根據本發明之較佳實施例，當排氣偵測裝置ιι〇，測 得碳氫化合物低於120 ppm時，脫硝級_智慧型全功能柴油 引擎廢氣處理系統丨會選擇第二廢氣處理路徑B，亦即先後 通過中間聯絡管10、氧化型觸媒除臭陣列3〇、選擇性還原 觸媒陣列150、消音器8〇、及排氣主管7〇，而後將淨化後 之廢氣排放至大氣，當排氣偵測裝置11〇，測得碳氫化合 物超過120 ppm時，脫硝級智慧型全功能柴油引擎廢氣處 理系統1會選擇第一廢氣處理路徑A，亦即先後通過中間聯 絡管10、下集管20、碳化矽除煙陣列5〇，氧化型觸媒除臭 陣列30、選擇性還原觸媒陣列15〇、及排氣主管7〇 ,而後 將淨化後之廢氣排放至大氣。 5. 根據本發明之較佳實施例，當排氣偵測裝置ιι〇，測 得一氧化碳低於300 ppm時，脫硝級智慧型全功能柴油引 擎廢氣處理系統丨會選擇第二廢氣處理路徑B，亦即先後通 過中間聯絡管10、氧化型觸媒除臭陣列3〇、選擇性還原觸 媒陣列150、消音器80、及排氣主管7〇而後將淨化後之廢 140426.doc •18- 201104062 :放=，氣。當排氣靖置，測得—氧化碳超過 會，::第一 Γ續級智慧型全功能柴油引擎廢氣處理系統1 後之廢氣排放至大氣 理路徑A，亦即先後通過中間聯絡管 :=0:炭化終煙陣列I氧化型觸媒除臭陣列 ^選㈣還原觸媒陣列15〇、及排氣管7〇，而後將淨化 6.根據本發明之較佳實施例，當排氣 得氮氧化物超過235ppm時，脫石肖級智慧型全功能毕油 擎廢氣處理系統1會選摆筮__ '、 " 廢氣處理路㈣，亦即先後通 =間_。：氧化型觸媒除臭陣列3。、選擇性還原觸 、列150、消音益8〇、及排氣主管7〇，而後將淨化後之 廢孔排放至大風。當排氣偵測裝置11〇，測得氮氧化物低 於235 _時，脫硝級智慧型全功能柴油引擎廢氣處理系 統1會選擇第-廢氣處理路徑A，亦即先後通過中間聯絡管 10、下集管20、碳化石夕除煙陣列5〇 ’氧化型觸媒除臭陣列 3〇、選擇性還原觸媒陣列15G、排氣管7()，而後將淨化後 之廢氣排放至大氣。 a 7.根據本發明之較佳實施{列，當#氣谓測裝置ιι〇，測 得氮氧化物超過235 Ppm時，脫靖級智慧型全功能柴油引 擎廢氣處理系統1 ’會起動氨氣產生加熱器162，將該固離 無機鹽類氨儲存器⑽適當加熱後，釋放出高純度的氨氣 (Amm〇ma Nh3) ’氨氣定量控制閥ΐ6ι以自動定量的方式注 入脫確級智慧型全功能柴油引擎廢氣處理系統中的選擇性 U觸媒陣列15〇 ’以處理氮氧化物⑽χ)，將其還原為氮 140426.doc J9- 201104062 氣與水後，排入大氣。 综上所述’排氣偵測裝置11 〇 ’將該等排氣資料傳輸至 微電腦控制器100，供微電腦控制器100判別污染程度後， 再由脫硝級智慧型全功能柴油引擎廢氣處理系統丨決定應 令廢氣通過第一廢氣處理路徑A或第二廢氣處理路徑8來 達成淨化廢氣之目的。 圖2所示為本發明之脫硝級智慧型全功能柴油引擎廢氣 處理系統1用來處理引擎廢氣之流程之示意圖。如圖i所 不，當引擎廢氣由入口端匕進氣、導入中間聯絡管1〇後， 一排氣偵測裝置110將廢氣之排氣資料傳送至微電腦控制 器100,用以判斷廢氣應導入第一廢氣處理路徑八或第二廢 氣處理路徑B。 若廢氣導入第一廢氣處理路徑A，經由 化錢煙陣列5。，氧化型觸媒除臭陣列3〇二= 媒陣列150。碳化矽除煙陣列5〇連接至一由一控制盤啟 動，再生加熱器（未顯示）及一空氣幫浦（未示）以必要時進 订奴化矽除煙陣列再生清理。在廢氣經氧化型觸媒除臭陣 歹J 30選擇性還原觸媒陣列15〇及碳化矽除煙陣列5〇淨化 後“涇過上集管60，由排氣主管7〇之出口端〇L排出。 右廢乳導入第二廢氣處理路徑B，進入氧化型觸媒除臭 陣列= ' 選擇性還原觸媒陣列⑼進行廢氣處理而後通 過’肖音态、經由排氣主管7〇之出口端OL排出。路徑選擇 工制閥9G可安裝於中間聯絡管1()與排氣主管川之間之適當 位置，較佳設於消音器8〇與排氣主管70之間。脫硝級智慧 I40426.doc -20- 201104062 型全功旎柴油引擎廢氣處系統1會令微電腦控制器100進行 廢氣最佳處理路徑選擇。路徑選擇控制閥90亦可如圖2所 示》又於氧化型觸媒除臭陣列30、選擇性還原觸媒陣列1 與消音器80之間。 此外，控制盤120較佳同時由一 Ups電源（不斷電電源） 13〇及一緊急電源140控制，可由一設於控制盤12〇内之微 處理控制器自動選擇電源種類’避免脫硝級智慧型全功能 柴油引擎廢氣處理系統i因跳電而無法操作。 圖3所示是本發明技術思想建構而成之另一實施例，其 顯示本發明採垂直對稱配置結構之實施狀態。如圖3所 示，脫确級智慧型全功能柴油引擎廢氣處理系統丨,大致包 括：一由元件編號為 10.，2〇.，3〇’，4〇.，5〇,，6〇,，川.，140426.doc 201104062 discloses a post-injection system for a hood, which can be installed on various old diesel vehicles, mainly composed of a diesel vaporizer and a filter, wherein the diesel vaporizer mainly vaporizes the diesel. The filter is mainly used to remove carbon monoxide, carbon chloride, micro particles, black smoke and odor by self-ignition and transition; Taiwan Patent Publication No. 577482 discloses a smoke purification and purification device. The heater of the unit is used as a catalytic converter because the temperature of the exhaust of the engine is insufficient, and the heating compensates for the short-term temperature rise; and the Taiwan Patent Publication No. M317493 discloses a diesel engine exhaust to improve the structure of the auxiliary heater after the pollution is improved. When the gas is introduced into the exhaust pipe, the fuel is extracted by the pressure difference, and after the atomization is ignited, the heat generated by the incompletely combusted exhaust gas discharged from the engine is reburned, and the smoke purification and purification filter is captured. The carbon particles are heated and burned again to enhance the function of removing smoke, deodorizing and detoxifying the purifier. In addition, regarding the treatment of toxic nitrogen oxides (Ν〇χ), the industry-known technology involves the selective catalytic reduction (SCR) to treat nitrogen oxides (10) X), when nitrogen oxides When (NOx) passes through the denitration catalyst, ammonia gas is used as a reducing agent used in the selective catalyst reduction method to convert nitrogen oxides (NOx) into nitrogen gas and water. * The following is a technique for treating toxic nitrogen oxides: U.S. Patent No. 5,489,420 discloses a technique for removing nitrogen oxides by adding a reducing agent to nitrogen oxides at a high temperature, wherein ammonia gas is used at 95 (rc) U.S. Patent Nos. 5,443,8,5 and 5,536,482 disclose the addition of a polymer to ammonia at 90 Torr to 12 Torr. Method for removing nitrogen oxides from gas; Taiwan Patent Publication No. 140426.doc 201104062 M271135 discloses a selective catalyst reduction denitration system which utilizes a reduction method to inject ammonia gas (Ammonia NH3) as a reducing agent, when nitrogen The oxide and ammonia gas flows through the catalyst bed, ie, the nitrogen oxides are reduced to nitrogen (Nj and water (Ηβ); and the Taiwan Patent Publication No. j 2485〇4 discloses an ammonia-adding subsystem including an ammonia vapor source and is disposed at the inlet. An ammonia injection grid in the pipeline, an ammonia vapor tube provided between the ammonia vapor source and the ammonia injection grid, a fluid passage, and a throttle valve disposed in the ammonia vapor tube, the step of mixing the ammonia vapor further comprises adding ammonia Controller The throttle valve controls the rate of ammonia addition. The sputum is black smoke. The purpose of the device is to transfer the solid carbon particles (Particulate), usually using a porous ceramic filter material. Therefore, when the black smoke exhaust enters the honeycomb passage through the inlet end of the filter, the outlet end of the passage is closed and cannot pass, and the carbon particles are captured by the honeycomb filter to achieve the effect of filtering the black smoke. Although the black smoke filter can achieve specific effects, in fact, there are still many disadvantages to treating the engine exhaust gas with such a green filter alone: (1) The black smoke filter can only filter black smoke, and the waste material must be shut down frequently. Clean up to avoid blockage, so it can't cooperate with the engine for a long time. (?) Honeycomb wall flow ms has a high pressure drop, so the number of traditional "black smoke filter" installed is also very large, system setting f It is very expensive to use about 5 to 5 times using an oxidizing catalyst converter. The purpose of the oxidizing catalyst converter (Diesel 〇xidati〇n Cataiyst) is to treat the gaseous state. Mosquito hydrogen (Hydr〇carb〇ns) and carbon monoxide (Carb〇n M〇noxlde). Oxidized catalyst coated on the surface of ceramic or metal base materials to reduce gaseous hydrocarbons (hydrocarbons) and oxidation 140426.doc 201104062 Carbon (Carbon M〇n〇xide) combustion temperature, then use the engine exhaust temperature to convert gaseous hydrocarbons (Hydr〇carb〇ns) and carbon monoxide (Carbon M〇noxide) into Water and carbon dioxide. However, the engine exhaust gas is only treated by the oxidized catalyst converter (Diesel 〇xidati〇n (5) (4)). (1) It cannot handle the large amount of black smoke generated when the engine is started instantaneously. (2) It cannot handle low engine load operation. At low exhaust temperatures (<25〇°c), the resulting gaseous hydrocarbons (Hydr〇carb_) and carbon monoxide (Carbon Monoxide) have disadvantages. Regarding the selective catalytic reduction (SCR) to treat toxic nitrogen oxides (N〇x), the diesel engine exhaust gas treatment technology known in the industry is immature and limited by changing engine loads and changes. Nitrogen oxide (Ν〇χ) emission concentration; especially when the engine is running at no load, the extremely low exhaust gas temperature (less than 25 °C -3GGt), the selective catalyst reduction method will not be able to proceed. Choose to use ammonia (eight jobs) 3 to reduce _, because ammonia is a toxic chemical, when the exhaust temperature is extremely low, because of the ineffective reduction of nitrogen oxides (Ν〇χ) There is a danger of gas spilling (Ammonia Slip). Although the wind is applied in the selective catalyst reduction (SCR) for denitration (DeNOx), it is a very good reducing agent, but its steam is 7.76 atm', its Buddha point is _33 4〇c, that is, at room temperature. Under normal pressure, it presents a chemical gas that is highly toxic and toxic. At high temperatures, it will decompose into flammable hydrogen and toxic gases, and the storage of ammonia in the fire will cause damage and explosion. Therefore, when the atmosphere is stored in the interior, safety must be carefully considered. Based on the above-mentioned limitations of 140,426.doc 201104062 and the safety considerations of ammonia storage, the currently known technology in the industry is aimed at the toxic nitrogen oxides contained in the exhaust gas of diesel engines discharged from generators or dynamic uninterruptible power systems. There is no economical and effective treatment technology in the part of 〇x). In addition, selective catalytic reduction (SCR), which uses ammonia as a reducing agent, is a technology known in the industry and is basically classified into two categories: "liquid ammonia" and "aqueous urea solution", as described below, whether it is liquid ammonia or urea. Aqueous solution still has many shortcomings and inconveniences in application: (1) Liquid ammonia (Liquefied Ammonia) (NH3) Liquid ammonia is not easy to store, and liquid ammonia should be stored in a pressure vessel at a pressure of 8 kg/cm2 or more. In the vaporization mode, the liquid ammonia is vaporized first, and then the ammonia gas is directly injected into the selective catalyst reduction (SCR) denitration device. The disadvantage is that the liquid ammonia is stored in a pressure vessel, and the pressure of the liquid ammonia is stored. The container 'is placed in the room (4) (4). If the ammonia gas leaks, the ammonia will mix with the air and there is a danger of explosion. (2) AqUeous Urea soluti〇nXc〇NH2 2 Urea exhibits a colorless crystalline solid shape at normal temperature and normal pressure and can be dissolved in water. The conventional method is to adjust the urea concentration in the aqueous urea solution to about 32.5%, and to reduce the nitrogen oxides (10) X) as a selective catalyst reduction method (scr). When the exhaust gas temperature is higher than 16 〇t, the spray is sprayed. Into the selective contact medium reduction method, the urea aqueous solution in the SCR denitration equipment will be decomposed into ammonia and carbon dioxide at high temperature, and the ammonia gas in the sputum will react with the I oxide to convert it into nitrogen and water. Discharge to the atmosphere. The disadvantages of urea include: (1) urinary sound, for, *β Λ J urea water/liquid mixture must be first decomposed into ammonia gas 140426.doc 201104062 and then denitration reaction (DeNOx) 'is an indirect ammonia injection method, Therefore, the reaction rate and efficiency of conversion from urea to ammonia are more difficult to control; (2) solid impurities are often generated in the injection nozzle portion, causing accumulation and nozzle clogging, which in turn affects the effect of nozzle spray; (3) Under normal temperature (35 ° C -60 ° C) 'There will be some urea aqueous solution decomposed into ammonia and carbon dioxide' is easy to cause ammonia leakage; (4) in low temperature environment (<_ 11 ° C ) 'Aqueous urea solution will cause condensation; and (5) Compared with liquid ammonia, 'has to be about 2.5_3 times the volume of space to store, and the effect of de-accuracy is not comparable to liquid ammonia. In summary, the related art relies on relying solely on a black smoke filter to filter solid fine carbon particles (Particulate) or to rely solely on an oxidized catalytic converter (Diesel Oxidation Catalyst) to treat gaseous hydrocarbons ( Hydrocarbons) and carbon monoxide (carbon Monoxide) or a black smoke filter coated with an oxidizing catalyst to simultaneously treat solid fine carbon particles (Particulate) and hydrocarbons (Carbon Monoxide), carbon monoxide (Carbon Monoxide), or It relies on liquid ammonia stored in a high-pressure pressure vessel, or a urea aqueous solution that requires a large-capacity storage space and many processing techniques, and is selectively treated by a catalytic reduction method (SCR); NOx). Whether using a black smoke filter (including catalyst coating), or using an oxidizing catalyst converter, or using a selective catalyst reduction (SCR) denitration device using liquid ammonia or aqueous urea as a reducing agent It is impossible to economically, safely and efficiently treat engine exhaust gases containing toxic nitrogen oxides (NOx), gaseous hydrocarbons (Hydrocarbons), carbon monoxide (carbon monoxide) and solid carbon particles (partculate) of 140426.doc 201104062. . Therefore, it is necessary to provide an automatic detection of exhaust gas pollution conditions, elastic, economical and effective use of carbonized strontium removal array, solid inorganic salt ammonia storage, selective reduction catalyst array and oxidizing catalyst deodorization The array, in addition to the above-mentioned common engine exhaust gas treatment know-how, comprehensively purifies pollutants in all engine exhaust gases including toxic nitrogen oxides (NOx), gaseous hydrocarbons (yocarbons), carbon monoxide (Carb〇n) M〇n〇xide) and solid-state fine carbon particles (Partieulate), which are specifically used in diesel engine exhaust gas treatment systems for generators or dynamic uninterruptible power systems. SUMMARY OF THE INVENTION The object of the present invention is to provide an advantage that the above-mentioned technical disadvantages can be overcome and applied to a generator or a dynamic uninterruptible power system, and the exhaust gas pollution can be automatically detected to flexibly, economically and effectively use carbon stone. Smoke Exhaust Array, Solid and Desalination Salt Storage, Selective Catalytic Array and Oxidation Catalyst: Array of denitrification intelligent full-featured diesel engine exhaust gas treatment system. The present invention integrates and improves the shortcomings of conventional black smoke filters and oxidizing catalyst converters, and combines an array of selected ammonia (SCR) with an advanced ammonia storage supply area to achieve full functionality. Catalyst ... Take the effect of the good calendar hole processing. The storage supply area of the present invention includes: solid-free (four)-type ammonia (four) device 140426.doc 201104062 ‘, 2004, 4 electric facilities air pollutant discharge standards. This month is about the denitration-grade intelligent full-month b wood oil engine exhaust gas treatment system including an exhaust gas flow area, which is used to process the engine = gas discharged from the engine. The exhaust gas flow region comprises: an intermediate communication pipe for introducing the engine exhaust gas into the exhaust gas flow region, 5, 丨, «, to the oxidized catalyst deodorizing array, at least one «reducing catalytic catalyst array, at least-carbonizing The wrong smoke array and the exhaust main e «Hai to vt-type catalytic deodorization array are directly or indirectly connected to the intermediate communication pipe' to treat hydrocarbons (carbonocarbons) or carbon monoxide from the intermediate communication pipe (Carb〇n application) The at least-selective reduction catalyst array is in direct or indirect communication with the intermediate communication tube, and the nitrogen oxide (Ν〇χ) exhaust gas from the intermediate contact officer is processed. The at least one carbonized fossil array is connected to the intermediate The tubes are directly or indirectly communicated to transition the exhaust gas from the intermediate communication tube containing solid fine carbon particles. The exhaust gas tray is indirectly or directly communicated with the carbonization stone removing array to pass the exhaust gas filtered through the carbonization stone removing array. Discharged to the atmosphere. The exhaust gas flow region defines a first exhaust gas treatment path and a second exhaust gas treatment path. The first exhaust gas treatment path and the first waste milk treatment road are extended Between the intermediate communication pipe and the exhaust gas line; and in the first exhaust gas treatment path, the exhaust gas passes through the intermediate liaison officer, the at least one carbonized stone smog array, and the at least one oxidation type catalyst deodorizing array The at least one selective reduction catalyst array, and the exhaust gas main body, and in the second exhaust gas treatment path, the exhaust gas passes through the intermediate contact e, the at least one oxidation type catalyst deodorizing array, the at least one selection The sexual reduction catalyst array, the smectic silencer and the exhaust main pipe. The exhaust gas flow area can detect an engine exhaust gas data by an exhaust gas detection device at an appropriate position, as 140426.doc -11- 201104062 After the engine exhaust enters the denitration-grade intelligent full-featured diesel engine gas treatment system via the intermediate communication pipe, the desulfurization-level intelligent full-featured diesel fuel recovery system can utilize a microcomputer controller to exhaust the engine. The data is made/out of the best judgment to determine that the engine exhaust gas is guided through the first exhaust gas treatment path from the second exhaust gas treatment path and then discharged to the atmosphere. According to the present invention, the exhaust gas is measured. The device is arranged in the path of the exhaust gas to continuously detect the exhaust gas data discharged by the engine, such as temperature and pressure, opacity, hydrocarbon, carbon monoxide, sulfur oxide, Nitrogen oxides, etc. The microcomputer controller then determines the degree of engine exhaust pollution based on the exhaust data, and issues an appropriate exhaust gas treatment path to achieve the best treatment effect 'black smoke particles, hydrocarbons, nitrogen oxides of the engine exhaust gas. And carbon monoxide, which is processed by a carbonized fossil ash array and an oxidizing catalyst deodorizing array and a selective reduction catalyst array. Further, the present invention further suggests that the carbonized fossil ash array adopts an automatically regenerated heating type black smoke. The filter, the oxidizing catalyst deodorizing array adopts a low-temperature catalytic converter, and replaces the conventional liquid oxygen, urea aqueous solution and the like with a solid-state inorganic salt ammonia trap. The advantage of the heated black smoke over the benefits is that the black smoke is treated with high efficiency and the coffin can be automatically regenerated; and the low temperature catalytic converter has the advantages of low cost of purchase, zero operating cost, and low carbon temperature τ, and carbon treatment. Hydrogen compounds, carbon monoxide and some of the smoke, the engine can run continuously' without stopping. The solid inorganic salt ammonia storage unit has the advantage of being able to safely and efficiently store high-purity ammonia (Ammonia NH3) and only cloud to _to, at a normal temperature and pressure, and to have a very small indoor storage space. After the above three devices are integrated by the system of the present invention, the expected effect can be obtained from 140426.doc 12·201104062. [Embodiment] FIG. 1 is a view showing an embodiment of a horizontal-to-spot structure of the present invention, in which the Qianshi Xiao-level intelligent full-function Chai pregnancy. .—The exhaust gas flow area consisting of 70 components numbered 10, 20, 3 150 ^ 40, 50, 6 〇, 7 〇, 8 〇, 15 〇 #, - numbered 160, "24 components Ammonia gas 1ηπ η to 1/, should be £, - microcomputer controller, and an exhaust gas detection device connected to the exhaust gas flow area, -,.Μ, 乳 milk gas storage supply area and microcomputer control βίοο e The exhaust gas flow area is as described above, preferably. 丨, A A 乂 I I I. - Intermediate communication pipe 10, to > one: header 20, at least one oxidation type catalyst deodorizing array 3 〇, at least a middle two" 4", at least - a carbonized smear array 50, at least one upper header 6 〇, a column ^ (Γ. main officer 7 〇, a silencer 8 〇, and at least one selective reduction catalyst array intermediate The communication pipe 1 has an inlet port IL connected to the engine exhaust port to discharge the untreated exhaust gas from the engine. The at least-lower header 20 causes the intermediate contact officer to The less oxidized catalyst deodorizing array 30 and the at least one selective reduction catalyst array 150 are in communication. The at least intermediate manifold 4 is configured to communicate the intermediate % conduit 1G with the at least - carbonized (four) tobacco array 5G. Thereby, the inter-contact liaison officer 10 can communicate with the at least one oxidation type catalyst deodorizing array 30, and, the, the selective reduction catalyst array 150 or the at least one carbonization and smoke removal array 5 。. The catalyst deodorizing array 30 and the at least one selective reduction catalyst array 150 and the niobium carbide de-smoking array 50 can communicate with each other through the intermediate header 40. H0426.doc -13- 201104062 Deoxidation of each oxidized catalyst The array 30' is preferably composed of at least one low temperature type catalytic converter, and is capable of obtaining the most desirable treatment effect when treating the carbon monoxide and hydrocarbon waste gas generated by the engine at a low load and a low exhaust temperature. The smoke removal array 50 is preferably composed of at least one heating type black smoke filter, which filters the black smoke at high efficiency and automatically regenerates the filter material, thereby obtaining the most optimal treatment effect. The ammonia storage supply area is preferably At least one solid inorganic salt The ammonia-like storage 2 160' is composed of at least one ammonia gas quantitative control valve 161 and at least one ammonia gas generating heater 1 62. The gas storage supply area can be high-purity ammonia gas in a safe and harmless manner under normal temperature and normal temperature. (Amm〇ni (NOx)' is the most ideal treatment effect. Each group of oxidized catalyst deodorizing arrays includes (1) low-temperature catalyst converter, and ammonia storage supply area 'better includes solid inorganic The salt ammonia storage device 16 〇, 12, an ammonia gas quantitative control valve ΐ6 ι, and the summer solstice 2 氨 ammonia generating heater 162. Each group of carbonized fossil ash array 5 〇, preferably 1 to 20 heating type A black smoke filter, and each set of selective reduction catalyst arrays 150, preferably included! To 2 () off 3 catalytic converter (1) e job Cata (four). As shown in the figure, in the preferred embodiment, when the denitration-grade intelligent full-function diesel exhaust gas treatment system 1 is used, the oxidation catalyst deodorizing array 3G and the solid inorganic salt are arranged in a symmetrical manner. Ammonia storage 16 〇, ammonia quantitative control m> Female, sentence 1 chyle generation heater 162, selective reduction catalyst array 150 and carbonization enthalpy smoke removal array 5 〇. Up to the upper header 6 〇 so that at least one carbonized fossil ash array 50 is connected to the exhaust main pipe I40426.doc 201104062 70, so that the purified gas discharged through the carbonization enthalpy removing array 5 可 can be circulated to the exhaust main pipe 70. The muffler 8 is connected to the at least one oxidation type catalyst deodorizing array 3, the selective reduction catalyst array 150 through the intermediate tube and the intermediate header 40, and provides a silencing function. In particular, as shown in Fig. 2, the exhaust gas flow zone defines a first exhaust gas treatment path A and a second exhaust gas treatment path 6 to treat different exhaust gases. The first exhaust gas treatment path A and the second exhaust gas treatment path: Lu B extend in the intermediate contact fl. And between the exhaust mains 7〇. As shown in Fig. 2, the first exhaust gas treatment path Α passes through at least a carbonization (four) (four) column 5 〇, at least one oxidation type catalyst deodorizing array 3 〇 and at least one selective reduction catalyst array 150. The second exhaust gas treatment path is passed through at least one oxidation type catalyst deodorizing array 30 and at least one selective reduction catalyst array (9). When the engine exhaust gas enters the de-class intelligent full-function diesel engine exhaust gas treatment system from the intermediate communication pipe 10, the microcomputer controller (10) can select a better exhaust gas treatment path according to the degree of engine exhaust pollution, that is, the first exhaust gas treatment path. Or the second exhaust gas treatment path Β 'for optimal exhaust gas treatment, and then discharged to the atmosphere. After the actual verification of the day and month, the processed engine money can meet the emission limit of China's non-road mobile machinery diesel exhaust pollutants for 2 years (China's second phase), 2015 European EUR0 4 environmental protection phase IV, 2Gu US耵 4 environmental protection four-stage off-highway diesel engine emission standards and 2004 Taiwan power facilities air pollutant discharge standards. In addition, the 'Stone-Shaping Intelligent Full-Featured Diesel Engine Exhaust Gas Treatment System m one step includes a path selection control valve 90 installed at an appropriate position between the intermediate communication pipe exhaust mains 7G. The path selection control valve 90 is controlled by the micro-power controller (10) to automatically select the first-to-exhaust gas treatment path A or the second exhaust gas treatment path B' to select the best way to treat the engine exhaust. In the first exhaust gas treatment path arranged by the denitration-grade intelligent full-function diesel engine exhaust gas treatment system 1, the exhaust gas passes through the intermediate communication pipe, the lower header 20, the carbonization annihilation array 5, and the oxidized catalyst. The deodorizing array 3〇 and the selective reduction catalyst array 150, and the exhaust main pipe 7〇. In the second exhaust gas treatment path B, the exhaust gas passes through the intermediate communication pipe 1〇, the oxidizing catalyst deodorizing array 30, the selective reduction catalyst array 15〇, the muffler (10), and the exhaust main carbonization enthalpy removing array. 5 〇, preferably at least one heated black smoke filter. The oxidizing catalyst deodorizing array 3 is preferably at least one low temperature type catalytic converter "selective reduction catalyst array 15", preferably at least one deNOx catalyst converter (De NOx Catalyst). In order to achieve optimum exhaust gas treatment, the ammonia storage supply zone preferably consists of at least one solid inorganic salt ammonia storage 160, at least one ammonia gas quantitative control valve 161 and at least one ammonia gas generating heater 16 2 . The exhaust gas detecting device 11 is disposed in the intermediate communication pipe 〇 to continuously detect the engine exhaust data before entering the first exhaust gas treatment path and the second exhaust gas treatment path, such as temperature, pressure, flow rate, and Light transmittance, hydrocarbons, carbon monoxide, sulfur oxides, nitrogen oxides, and the like. How the exhaust gas detecting device 110 detects the exhaust gas exhaust data is provided to the microcomputer controller 100 to select an appropriate exhaust gas processing path, as exemplified as follows. 1 . According to a preferred embodiment of the present invention, when exhaust gas is detected Measuring device i 10, measuring and discharging * When the temperature exceeds 2 5 0 C, the denitration-grade intelligent full-function diesel engine 140426.doc -16 - 201104062 The exhaust gas treatment line will select the second exhaust gas treatment path B, that is, pure The exhaust gas is discharged to the atmosphere through the intermediate communication pipe H), the oxidizing catalyst deodorizing array 3G, the selective reduction catalyst array 150, the muffler 80, and the exhaust main pipe 7〇. If the exhaust gas detecting device 110 detects that the exhaust gas temperature is lower than the measured force, the exhaust gas processing system of the de-level intelligent full-function diesel engine engine selects the first exhaust gas treatment path A, that is, passes through the intermediate communication pipe 1〇. The lower header 2〇, the tantalum carbide deodorization array 50, the oxidizing catalyst deodorizing array 3〇, the selective reduction catalyst array, and the exhaust main pipe 7G, and then the treated exhaust gas is discharged to the atmosphere. 2. According to a preferred embodiment of the present invention, when the exhaust gas detecting device is ιι〇, it is determined that the exhaust system pressure exceeds the maximum allowable exhaust pressure of the engine (―Engine An〇Wable Back p ure) The full-featured diesel engine exhaust gas treatment system m selects the second exhaust gas treatment path B, that is, through the intermediate communication pipe 10, the oxidizing catalyst deodorizing array 30, the selective reduction catalyst array 150, the muffler 8〇, and The exhaust main pipe is 7 〇, and then the treated exhaust gas is discharged to the atmosphere. When the exhaust gas detection device is 〇, and the exhaust system pressure is lower than the maximum allowable exhaust pressure of the engine, the desulfurization-class intelligent full-function diesel engine exhaust gas treatment system (6) will select the _ exhaust gas treatment path A, that is, It has passed through the intermediate communication pipe 10, the lower header 2〇, the carbonized stone de-smoke array 5〇, the oxidized catalyst deodorizing array 3〇, the selective reduction catalyst matrix 10(10)' exhaust main controller 70, and then processed The exhaust gas is discharged to the atmosphere. 3. According to a preferred embodiment of the present invention, when the exhaust system (10) is measured to have a light transmittance exceeding that of Cong, the 'disintegrated intelligent full-function diesel engine waste milk treatment system 1 will select the first exhaust gas treatment path A. (4) successively passed the liaison officer 10 in the H0426.doc 201104062, the lower header 20, the carbonized annihilation array 5 〇, the oxidized catalyst deodorizing array 3〇, the selective reduction catalyst array 150, and the exhaust supervisor 7 〇, and then the treated exhaust gas is discharged to the atmosphere. If the exhaust (4) device is ιι〇, and the measured opacity is less than 20%, the denitration-grade intelligent full-featured diesel engine exhaust gas treatment system 1 will select the second exhaust gas treatment path B, that is, through the intermediate communication pipe. 10. Oxidation-type catalyst deodorizing array 3〇, selective reduction catalyst array 150, > phonograph 8G, and exhaust main pipe 7(), and then discharging the treated exhaust gas to the atmosphere. 4. According to the present invention In a preferred embodiment, when the exhaust gas detecting device is ιι〇 and the hydrocarbon is less than 120 ppm, the denitration level intelligent multi-function diesel engine exhaust gas treatment system selects the second exhaust gas treatment path B, That is, the intermediate communication pipe 10, the oxidizing type catalyst deodorizing array 3〇, the selective reduction catalyst array 150, the muffler 8〇, and the exhaust main pipe 7〇 are successively discharged, and then the purified exhaust gas is discharged to the atmosphere, and is discharged. The gas detecting device 11〇, when the hydrocarbon is more than 120 ppm, the denitration-grade intelligent full-function diesel engine exhaust gas treatment system 1 selects the first exhaust gas treatment path A, that is, through the intermediate communication pipe 10 and the lower set Tube 20, carbonized enthalpy smoke removal array 5〇, Catalyst type of deodorant array 30, the array 15〇 selective reduction catalyst, and an exhaust competent 7〇, and then the purified exhaust gas is discharged to the atmosphere. 5. According to a preferred embodiment of the present invention, when the exhaust gas detecting device is ιι, the carbon monoxide is less than 300 ppm, the denitration-grade intelligent full-function diesel engine exhaust gas treatment system selects the second exhaust gas treatment path B. , that is, through the intermediate communication pipe 10, the oxidizing catalyst deodorizing array 3 〇, the selective reduction catalyst array 150, the muffler 80, and the exhaust main pipe 7 〇 and then the purified waste 140426.doc • 18- 201104062 : Put =, gas. When the exhaust gas is set, the measured carbon monoxide exceeds the meeting.:: The exhaust gas after the first 智慧Synchronous Intelligent Full-Featured Diesel Engine Exhaust Gas Treatment System 1 is discharged to the atmospheric path A, that is, through the intermediate communication pipe: 0: carbonized final smoke array I oxidizing catalyst deodorizing array ^ (4) reducing catalyst array 15 〇, and exhaust pipe 7 〇, and then purifying 6. According to a preferred embodiment of the present invention, when exhausting nitrogen When the oxide exceeds 235ppm, the desulfurization-level intelligent full-featured oil-fired exhaust gas treatment system 1 will select the 筮__ ', " exhaust gas treatment road (4), that is, the pass_between. : Oxidation type catalyst deodorizing array 3. Selective reduction touch, column 150, silencer 8 〇, and exhaust main 7 〇, then the purified waste hole is discharged to the strong wind. When the exhaust gas detecting device 11 detects that the nitrogen oxide is lower than 235 _, the denitration-grade intelligent full-function diesel engine exhaust gas treatment system 1 selects the first exhaust gas treatment path A, that is, passes through the intermediate communication pipe 10 The lower header 20, the carbonized stone de-smoke array 5〇' oxidized catalyst deodorizing array 3〇, the selective reduction catalyst array 15G, the exhaust pipe 7 (), and then the purified exhaust gas is discharged to the atmosphere. a 7. According to a preferred embodiment of the present invention {column, when the gas measuring device ιι〇, the measured nitrogen oxides exceed 235 Ppm, the degassing level intelligent full-function diesel engine exhaust gas treatment system 1 'will start ammonia gas The heater 162 is generated, and the solid-state inorganic salt ammonia storage device (10) is appropriately heated to release high-purity ammonia gas (Amm〇ma Nh3). The ammonia gas quantitative control valve ΐ6ι is injected into the decisive level wisdom in an automatic quantitative manner. The selective U catalyst array in the full-featured diesel engine exhaust gas treatment system is treated to treat nitrogen oxides (10), which is reduced to nitrogen 140426.doc J9-201104062 and then discharged into the atmosphere. In summary, the 'exhaust gas detecting device 11 〇' transmits the exhaust gas data to the microcomputer controller 100 for the microcomputer controller 100 to determine the degree of pollution, and then the denitration-grade intelligent full-function diesel engine exhaust gas treatment system. It is determined that the exhaust gas should pass through the first exhaust gas treatment path A or the second exhaust gas treatment path 8 for the purpose of purifying the exhaust gas. Fig. 2 is a schematic view showing the flow of the denitration-grade intelligent full-function diesel engine exhaust gas treatment system 1 for treating engine exhaust gas according to the present invention. As shown in FIG. 1 , after the engine exhaust gas is taken in from the inlet port and introduced into the intermediate communication pipe 1 , an exhaust gas detecting device 110 transmits the exhaust gas data of the exhaust gas to the microcomputer controller 100 to determine that the exhaust gas should be introduced. The first exhaust gas treatment path eight or the second exhaust gas treatment path B. If the exhaust gas is introduced into the first exhaust gas treatment path A, it passes through the money smoke array 5. Oxidation type catalyst deodorizing array 3 〇 2 = media array 150. The tantalum carbide de-smoke array 5 is connected to a start-up panel, a regenerative heater (not shown) and an air pump (not shown) for re-storing the slagging and removing the smoke array if necessary. After the exhaust gas is oxidized by the oxidizing catalyst deodorizing array J 30 selective reduction catalyst array 15 〇 and the carbonized 矽 矽 阵列 阵列 阵列 〇 〇 〇 〇 〇 〇 泾 泾 泾 上 上 上 上 上 上 上 上 上 上 上 上 上 上 上 上 上 上Discharge. The right waste milk is introduced into the second exhaust gas treatment path B, and enters the oxidizing catalyst deodorizing array = 'Selective reduction catalyst array (9) for exhaust gas treatment and then passes through the 'Xiaoyin state, via the exhaust terminal 7's outlet end OL Discharge. The path selection valve 9G can be installed at an appropriate position between the intermediate communication pipe 1 () and the exhaust main pipe, preferably between the muffler 8 〇 and the exhaust main pipe 70. Denitration level wisdom I40426. Doc -20- 201104062 Full-power diesel engine exhaust system 1 will enable the microcomputer controller 100 to select the optimal exhaust gas path. The path selection control valve 90 can also be deodorized by the oxidizing catalyst as shown in Figure 2. The array 30, the selective reduction catalyst array 1 and the muffler 80. In addition, the control panel 120 is preferably controlled by an Ups power supply (continuous power supply) 13〇 and an emergency power supply 140, and can be disposed on the control panel. The microprocessor controller within 12〇 automatically selects the power supply type 'Avoiding the denitration-grade intelligent full-featured diesel engine exhaust gas treatment system i is inoperable due to power jump. FIG. 3 is another embodiment of the technical idea of the present invention, which shows that the present invention adopts a vertical symmetric configuration structure. The state of implementation. As shown in Fig. 3, the exhaust-level intelligent full-function diesel engine exhaust gas treatment system 大致, generally includes: a component number is 10., 2〇., 3〇', 4〇., 5〇, 6〇,,川.,
50等構件組成之廢氣流動區、一微電腦控制器 100·、一由元件編號為160，，161，，162.等構件組成之氨氣 儲存供應n連接於廢氣流動區、氨氣儲存供應區、 微電腦控制器100’之間之排氣偵測裝置丨1〇,。此外，一左 集管仆’及一右集管42,分別架設於上集管6〇.、下集管π,之 間、並各位於中間集管40，之左右側。 心月亦可以其他的特定形4來實⑯’而不脫離本發明 之精神和4要特性°因此上文所狀實施例在各方面都應 認為是例示性而非限制性，而所有之改變只要合乎申請專 利範圍之意義和範圍或其等效者’均應包含在本發明的範 疇之内。 【圖式簡單說明】 140426.doc •21 · 201104062 系 系 圖1係本發明脫硝級智慧型全功能柴油引擎廢氣處理 統採水平對稱配置結構之一實施例。 圖2顯示圖1實施例之示意圖。 圖3係本發明脫硝級智慧型全功能柴油弓丨擎廢氣處理 統採垂直對稱配置結構之另一實施例。 【主要元件符號說明】 1，1' 脫硝級智慧型全功能柴油？丨擎廢氣處 系統 10 « 10' 中間聯絡管 20，20' 下集管 30，30' 氧化型觸媒除臭陣列 40，40' 中間集管 41 左集管 42' 右集管 50 > 50' 碳化矽除煙陣列 60 > 60' 上集管 70，70' 排氣主管 80，80' 消音器 90，90' 路徑選擇控制閥 100 « 100' 微電腦控制器 110，110， 排氣偵測裝置 120，120' 控制盤 130 ups電源 140 緊急電源 理 140426.doc -22- 201104062 150， 150’ 選擇性還原觸媒陣列 160， 160， 固態無機鹽類氨儲存器 161， 161' 氨氣定量控制閥 162， 162' 氨氣產生加熱器 A 第一廢氣處理路徑 B 第二廢氣處理路徑 IL 入口端 OL 出口端 140426.doc -23-An exhaust gas flow region composed of 50 components, a microcomputer controller 100, an ammonia gas storage supply consisting of components such as 160, 161, 162. is connected to the exhaust gas flow region, the ammonia gas storage supply region, The exhaust gas detecting device between the microcomputer controller 100' is 〇1〇. In addition, a left header servant' and a right header 42 are respectively disposed between the upper header 6〇 and the lower header π, and are located on the left and right sides of the intermediate header 40, respectively. The heart and the moon may also be exemplified by other specific forms without departing from the spirit and scope of the invention. Therefore, the above embodiments are to be considered in all respects as illustrative and not restrictive, The meaning and scope of the claims and the equivalents thereof are intended to be included within the scope of the invention. [Simple description of the drawings] 140426.doc •21 · 201104062 System Fig. 1 is an embodiment of the horizontally symmetric configuration of the exhaust gas treatment system of the denitration-grade intelligent full-function diesel engine of the present invention. Figure 2 shows a schematic view of the embodiment of Figure 1. Fig. 3 is another embodiment of the vertical symmetric configuration of the denitration-grade intelligent full-function diesel diesel engine. [Main component symbol description] 1,1' Denitration-grade intelligent full-featured diesel?丨 废气 exhaust system 10 « 10' intermediate communication pipe 20, 20' lower header 30, 30' oxidizing catalyst deodorizing array 40, 40' intermediate header 41 left header 42' right header 50 > 50 'Carbide ash removal array 60 > 60' Upper header 70, 70' Exhaust main 80, 80' Silencer 90, 90' Path selection control valve 100 « 100' Microcomputer controller 110, 110, Exhaust detection Device 120, 120' control panel 130 ups power supply 140 emergency power supply 140426.doc -22- 201104062 150, 150' selective reduction catalyst array 160, 160, solid inorganic salt ammonia storage 161, 161' ammonia quantitative control Valve 162, 162' ammonia gas generating heater A first exhaust gas treatment path B second exhaust gas treatment path IL inlet end OL outlet end 140426.doc -23-