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TW200533651A - Process and apparatus for the removal of nitrogen compounds from a fluid stream - Google Patents

Process and apparatus for the removal of nitrogen compounds from a fluid stream Download PDF

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Publication number
TW200533651A
TW200533651A TW93139426A TW93139426A TW200533651A TW 200533651 A TW200533651 A TW 200533651A TW 93139426 A TW93139426 A TW 93139426A TW 93139426 A TW93139426 A TW 93139426A TW 200533651 A TW200533651 A TW 200533651A
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Taiwan
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stream
line
alkylation
benzene
matrix
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TW93139426A
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Chinese (zh)
Inventor
Robert J Schmidt
Andrew S Zarchy
Gregory J Gajda
Guy B Woodle
Deng-Yang Jan
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Uop Llc
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Priority claimed from US10/740,872 external-priority patent/US7205448B2/en
Priority claimed from US10/741,470 external-priority patent/US6894201B1/en
Application filed by Uop Llc filed Critical Uop Llc
Publication of TW200533651A publication Critical patent/TW200533651A/en

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Abstract

Disclosed is a process and apparatus for removing nitrogen compounds from an alkylation substrate such as benzene. A conventional adsorbent bed (46, 114) can be used to adsorb basic organic nitrogen compounds and a hot adsorbent bed (72, 162) of acidic molecular sieve can adsorb the weakly basic nitrogen compounds such as nitriles. Water facilitates the adsorption of the weakly basic nitrogen compounds. Running an alkylation substrate stream (68, 8) from a fractionation column (40, 130) of elevated temperature and suitable water concentration to the hot adsorbent bed may be advantageous.

Description

200533651 九、發明說明: 【發明所屬之技術領域】 本發明係關於一種自产娜必^ 自L 物〜移除氮化合物之方法及裝 置°特別地,本發明传 η一 f ㈣關以擇性吸附方法的用途,用來 自fe物>;IL移除骑類, # 、^保道方香無轉化觸媒。 本發明的另一個目的是提一 、 疋促t、個保蠖床,其從烷化或轉 义元化區域的烴進料流中 竹飢T在水的存在下吸附腈類。 本發明的另一個目县:¾ /j£工An ^ 目的疋^供兩個不同組合物的保護床, 其能合作地從烴進料流中吸附〇NCs。 【先前技術】 分子筛在芳香族轉化製程中用做觸媒,在化學製程及煉 油工業中為已熟知的。相當商業重要性的芳香族轉化反應 包括芳香化合物的烷基化,士口 :在乙基甲苯、二甲苯、乙 基本、異丙苯、或高碳烧基芳香族的生產中及岐化反應 中丄如:甲苯岐化、二甲苯異構化、或多院基苯類轉烧化 成單烷基苯類。通常到芳香族轉化製程的進料會包括芳香 組份或烧基化基質,如:苯、及c2K2Q烯烴燒化劑、多 烧基芳香烴轉化劑。在烧化區域中,料族進料流及煙系 進料流在烷化觸媒上反應,產生烷化苯,如:乙基苯或異 丙苯。多烷基苯類從單烷基苯產物中分離,並且回收到轉 烷化區域,並且與苯在轉烷化觸媒上接觸,產生單烷基苯 類及苯。 此類烧化或轉烧化反應的觸媒通常包括沸石分子筛。美 國專利1^4,891,458揭示觸媒的存在,包含沸石(3。美國專 98299.doc 200533651 利US 5,03G,786揭示-種使用沸石γ、及沸μ分子 篩觸媒的芳香族轉化製程。美國專利US 4,185,040揭示苯 的烷化,產生乙基苯或異丙苯,使用如:χ、γ、[、B、 ZSM-5及ω結晶型之分子篩的沸石。美國專利us 4,774,仍 揭示一種芳香族轉化製程,牽涉到在包含固體磷酸組份之 觸媒上的烷化、續以轉烷化,使用包括χ、γ、超穩定Y、 L、ω及絲光沸石的鋁矽酸鹽分子篩轉烷化觸媒。 水通常被發現在烷化及轉烷化反應中的芳香族進料裡, 特別在苯進料中。苯進料通常是經水飽和的,例如··當其 從苯乙稀單體單元回收時。在氣或液相之烧化反應中使用 的分子篩觸媒’會是對進料中不同份量的水或硫化合物敏 感的。關專利US 4,1G7,224揭示:若觸媒的更快速老化 為可接受的,則在氣相反應中的水及硫化氫為可忍受的。 美國專利US 5,()3(),7_示:當反應區域被操作在維持反 應器内容物於液相時,進料的脫水到水含量不多於 ppm,並且較佳為5〇 ppm或更低。然而,w〇 93/⑼的二揭 示在起始相中,用於烷化或轉烷化製程中的沸石觸媒必須 具有最低水含量不多於3.5重量%,是相對於觸媒組合物。 EP 〇 922 020 B1揭示固體酸的使用,從苯烷化進料中吸附 不純物,其在13(TC及30(TC之間的溫度下被乾燥到包含不 多於200 ppm的水,以改進沸石烷化或轉烷化觸媒的壽 命。 存在於對芳香族轉化反應器之進料當中的其他不純物, 特別是鹼性不純物,如··鹼性有機氮化合物(〇NCs),中和 98299.doc 200533651 了包括大部份現今之芳香族烧化觸媒的固體酸。 及觸媒壽命被負面地影響。在累積的氮化合物期間^進 枓:甚至是非常低氮化合物,增加了觸媒再生頻率,並且 焦炭必須從觸媒燃燒。更活性的沸石觸媒被使用於芳香族 轉化反應中,在進料中之氮不純物使觸媒壽命減退,必須 被更小心地控制。尋求減少反應區域中觸媒上之氮不純物 影響的製程。降低觸媒壽命之驗性氣化合物包括+朵類、 吡啶類、喹仙、二乙醇胺(DEA)、嗎啉類,包括n_甲醯 基_ Μ⑽M)及N_甲基_四氫NMp)。刪及請 被用做芳香族萃取劑’並且DEA為腐蝕抑制劑,其通常都 污染芳香族進料流。美國專利us 5,22M99教導以沸石類 移除十朵、喹啉及吡啶不純物’並且使用甲苯與溶解的 水’從沸石中脫附不純物。w〇⑼⑽娜示將烧化苯血 分子筛接觸,在將其進料到轉炫化反應器之前移除包括氮 化合物的觸媒毒素。wo 〇1/〇7383揭示將到烧化區域的進 料流與彿石接觸,移除有機鍵結的氮。美國專利仍 4,846,962揭示將溶劑萃取油與無結晶性氧化矽-氧化鋁、 或結晶性沸石吸附劑接觸,移除如:NMP之鹼性氮化合 物。該吸附劑可包括高至3〇重量%的水。 口 美國專利US 5,271,835揭示在來自流體催化性裂解單元 之C3至C5產物份中存在極性不純物。該不純物被發現包 括士乙%的弱鹼性0NCs。丙烯腈及丙腈也可發現於烴 物流中’其做為到芳香族烧化製程的進料。這些極性化合 物吸附到並且母化使用於芳香族垸化製程的觸媒。美國專 98299.doc 200533651 利US 6,019,887教導在不高於300°C下使用陽離子非酸性沸 石,並且美國專利US 6,107,535教導使用氧化矽膠,在室 溫下從烴物流中吸附腈類。美國專利US 2,999,861教導使 用X沸石,在-18至427X:下選擇性地吸附鹼性〇NCs,超越 包括腈類、硝酸鹽及硝基化合物的弱鹼性〇NCs。美國專 利US 5,744,686及美國專利US 5,942,650教導在移除腈類之 前’從包含腈類的苯物流中移除水,是藉著將苯物流與非 酸性分子篩在-18°C至204°C下接觸。US 6,617,482 B1教示 當存有水時,較高二氧化矽之沸石較為有效。然而,在水 存在下,證實在室溫下只吸附NFM ;在此文獻申,腈類的 吸附被證實只在無水存在下。在每百萬之份數及每十億之 份數之範圍内的低濃度腈類,會累積地使烷化觸媒諸如結 焦之其他失活機制更快失活。 黏土或樹脂保護床是從芳香族烧化進料流中吸附〇ncs 的便宜方式。在從烷化進料流中吸附有機氮的期間,焦炭 也在吸附劑上形成。當所有的吸附位置被0NCsa焦炭佔 據時,這些吸附劑變成失效的。失效的黏土及樹脂保護床 不能以燃燒再生。包含分子篩的保護床可以從吸附劑燃燒 掉ONCs及焦炭而被再生。 【發明内容】 我們發現:如黏土及樹脂物質的習用吸附劑不足以在水 的存在下從烴物流中吸附腈類。我們進一步發現:在較低 溫度下,酸性分子篩吸附劑較佳地吸附水及鹼性〇NCs, 而超越弱鹼性ONCs,如在烴物流中的腈類。然而,升溫 98299.doc 200533651 改進酸性分子篩吸附劑在水 丁你r對月月類的吸附能力。 假設:酸性分子篩在升溫 _ ^ ^ 田做觸媒來水解腈成胺或醯 後,該驗性胺或醢胺被強烈地吸附在酸性分子筛 2 °因此’習用吸附劑可制來吸附A部份的有機氮不純 物’亚且酸性分子筛可用來吸附維持弱驗性的有機氮化合 物,如:腈類。再者,來自分館塔的煙物流會具有適當的 水濃度及溫度,以加速腈類被酸性分子篩吸附。當失效 時,該分子筛可被再生。我們也發現:水的存在也減輕焦 厌在吸附劑上的累積,因此延長再生循環。 【實施方式】 本發明的烴進料流通常是液體,並且可包含從30 wppb 至1莫耳/〇的ONCs,並且一般為丨〇 w卯b至丨⑻的 〇NCs。本發明證實能夠吸附存在每百萬之份數範圍内濃 度的ONCs ϋ且我們相^ :其能有效地抵銷在下游觸媒 上每十億之份數範圍内的0NC濃度。該烴進料流可包含 水,高至並超越飽和條件。包含〇NCs及水的烴進料流可 為芳香族進料流,較佳包括苯,並且適當地主要為苯。當 其流過吸附劑床時,該芳香族進料流一般包括不超過1〇 重量%的烯烴。 ONCs —般包括較大比例的鹼性〇NCs,如:啕哚類、吡 啶類、喹啉類、一乙醇胺(DEA)、嗎啉類,包括N-曱醯基_ 嗎啉(NFM)及N-曱基-四氫吡咯酮(NMp)。〇NCs&可包括 較少比例的弱鹼性腈類,如:乙腈、丙腈、丙烯腈及其混 合物。該鹼性ONCs被良好地吸附在習用的黏土或樹脂吸 98299.doc -10- 200533651200533651 IX. Description of the invention: [Technical field to which the invention belongs] The present invention relates to a method and a device for producing nitrogen compounds from L compounds to removing nitrogen compounds. In particular, the present invention conveys the η-f threshold to selectivity. The application of the adsorption method is to remove the riding class with Fe> IL, and #, ^ 保 道 方 香 No conversion catalyst. Another object of the present invention is to provide a hydration-enhancing bed that absorbs nitriles from the hydrocarbon feed stream in the alkylation or escape metathesis zone in the presence of water. Another objective of the present invention is to provide a protective bed for two different compositions that can cooperatively adsorb ONCs from a hydrocarbon feed stream. [Previous Technology] Molecular sieves are used as catalysts in aromatic conversion processes, and are well known in chemical processes and the refining industry. Commercially important aromatic conversion reactions include the alkylation of aromatic compounds, Shikou: in the production of ethyl toluene, xylene, ethyl ethyl, cumene, or high-carbon aromatic aromatics and disproportionation reactions For example: disproportionation of toluene, isomerization of xylene, or trans-firing of multi-base benzenes into monoalkylbenzenes. Generally, the feed to the aromatic conversion process will include aromatic components or calcined substrates, such as: benzene, and c2K2Q olefin calcining agents, multi-carbon based aromatic hydrocarbon converting agents. In the firing zone, the feedstock stream and the smoke-based feedstream react on the alkylation catalyst to produce alkylated benzenes, such as ethylbenzene or isopropylbenzene. Polyalkylbenzenes are separated from the monoalkylbenzene product and recovered to the transalkylation zone and contacted with benzene on the transalkylation catalyst to produce monoalkylbenzenes and benzene. Catalysts for such calcination or trans-calcination reactions typically include zeolite molecular sieves. U.S. Patent No. 1,891,458 discloses the existence of catalysts, including zeolites (3. US Patent 99299.doc 200533651 and US 5,03G, 786 discloses an aromatic conversion process using zeolite gamma and boiling μ molecular sieve catalysts. U.S. Patent No. 4,185,040 discloses the alkylation of benzene to produce ethylbenzene or cumene, using zeolites of molecular sieves such as χ, γ, [, B, ZSM-5 and ω. U.S. Patent No. 4,774, still Revealing an aromatic conversion process involving alkylation on a catalyst containing a solid phosphoric acid component, followed by transalkylation, using aluminosilicates including χ, γ, ultra-stable Y, L, ω, and mordenite Molecular sieves are converted to alkylation catalysts. Water is usually found in aromatic feeds in alkylation and transalkylation reactions, especially in benzene feeds. Benzene feeds are usually saturated with water, for example, when When recovering styrene monomer units, the molecular sieve catalysts used in the gasification or liquid phase calcination reaction will be sensitive to different amounts of water or sulfur compounds in the feed. The related patent US 4,1G7,224 discloses: If faster aging of the catalyst is acceptable, then in a gas phase reaction Water and hydrogen sulfide are tolerable. US patent US 5, () 3 (), 7_ shows that when the reaction zone is operated to maintain the reactor contents in the liquid phase, the feed is dehydrated to not more than water content ppm, and preferably 50 ppm or less. However, the two of WO 93 / ⑼ reveal that in the starting phase, the zeolite catalyst used in the alkylation or transalkylation process must have a minimum water content of not much. At 3.5% by weight, it is relative to the catalyst composition. EP 〇922 020 B1 discloses the use of a solid acid, which adsorbs impurities from a benzene alkylation feed, which is dried at a temperature between 13 ° C and 30 ° C To contain no more than 200 ppm of water to improve the life of the zeolite alkylation or transalkylation catalysts. Other impurities present in the feed to the aromatic conversion reactor, especially alkaline impurities such as alkali Organic nitrogen compounds (ONCs), neutralizing 98299.doc 200533651 including most of the solid acids of today's aromatic burning catalysts. And catalyst life is negatively affected. During the accumulation of nitrogen compounds ^ into: Even very low nitrogen compounds increase the frequency of catalyst regeneration, and Must be burned from the catalyst. More active zeolite catalysts are used in the aromatic conversion reaction. The impure nitrogen in the feed will reduce the catalyst life and must be controlled more carefully. Seek to reduce the amount of catalyst on the catalyst in the reaction area. Processes affected by nitrogen impurities. Test gas compounds that reduce catalyst life include + flowers, pyridines, quinoxanes, diethanolamine (DEA), morpholine, including n_methylamyl_M⑽M) and N_methyl _Tetrahydro NMp). Please delete it as an aromatic extractant and DEA is a corrosion inhibitor, which usually pollutes the aromatic feed stream. US Patent US 5,22M99 teaches the removal of ten quinones and quinoids with zeolites. The phthaloline and pyridine impurities were desorbed from the zeolite using toluene and dissolved water. Woo Na showed that the benzene zeolite molecular sieves were contacted, and the catalyst toxins including nitrogen compounds were removed before feeding them to the transfection reactor. wo 〇1 / 〇7383 discloses that the feed stream to the calcination zone is contacted with the spar to remove organically-bonded nitrogen. U.S. Patent No. 4,846,962 discloses contacting a solvent-extracted oil with a non-crystalline silica-alumina, or a crystalline zeolite adsorbent to remove alkaline nitrides such as NMP. The sorbent may include up to 30% by weight of water. U.S. Patent No. 5,271,835 discloses the presence of polar impurities in the C3 to C5 product fractions from the fluid catalytic cracking unit. The impurities were found to include weakly basic 0NCs in ethyl acetate. Acrylonitrile and propionitrile can also be found in the hydrocarbon stream ' as a feed to the aromatic firing process. These polar compounds are adsorbed and mother catalysts used in the aromatic tritiation process. U.S. Patent No. 98299.doc 200533651, US 6,019,887 teaches the use of cationic non-acid zeolites at temperatures not higher than 300 ° C, and U.S. Patent No. 6,107,535 teaches the use of silica to adsorb nitriles from a hydrocarbon stream at room temperature. U.S. Patent No. 2,999,861 teaches the use of X zeolites to selectively adsorb basic oNCs at -18 to 427X :, exceeding weakly basic oNCs including nitriles, nitrates and nitro compounds. U.S. Patent No. 5,744,686 and U.S. Patent No. 5,942,650 teach 'removing water from a benzene stream containing nitriles prior to removing nitriles by contacting the benzene stream with a non-acidic molecular sieve at -18 ° C to 204 ° C . US 6,617,482 B1 teaches that zeolites with higher silica are more effective when water is present. However, in the presence of water, it was confirmed that only NFM was adsorbed at room temperature; in this document, it was confirmed that the adsorption of nitriles was confirmed only in the absence of water. Low concentrations of nitriles in the range of parts per million and parts per billion will cumulatively deactivate alkylation catalysts such as coking and other inactivation mechanisms faster. Clay or resin guard beds are a cheap way to adsorb Oncs from an aromatic calcined feed stream. During the adsorption of organic nitrogen from the alkylation feed stream, coke is also formed on the adsorbent. When all the adsorption sites are occupied by 0NCsa coke, these adsorbents become ineffective. Failure of clay and resin protection beds cannot be regenerated by combustion. Protective beds containing molecular sieves can be regenerated by burning off ONCs and coke from the adsorbent. [Summary of the invention] We have found that conventional adsorbents such as clay and resinous substances are not sufficient to adsorb nitriles from hydrocarbon streams in the presence of water. We further found that at lower temperatures, acidic molecular sieve adsorbents better adsorb water and alkaline ONCs, and surpass weakly basic ONCs, such as nitriles in hydrocarbon streams. However, increasing the temperature of 98299.doc 200533651 improves the adsorption capacity of acidic molecular sieve adsorbents on water and moons. Assumption: After the acidic molecular sieve is heated up as a catalyst to hydrolyze nitrile to amine or amidine, the test amine or amidine is strongly adsorbed on the acidic molecular sieve 2 °, so 'conventional adsorbent can be prepared to adsorb part A Organic nitrogen impure substances and subacidic acid molecular sieves can be used to adsorb organic nitrogen compounds that maintain weak sensitivity, such as nitriles. Moreover, the smoke stream from the branch tower will have an appropriate water concentration and temperature to accelerate the adsorption of nitriles by the acid molecular sieve. When it fails, the molecular sieve can be regenerated. We have also found that the presence of water also reduces the build-up of anxiety on the adsorbent, thus extending the regeneration cycle. [Embodiment] The hydrocarbon feed stream of the present invention is usually a liquid, and may contain ONCs from 30 wppb to 1 mol / o, and generally ○ NCs from 〇0 w 卯 b to ⑻⑻. The present invention proves that it can adsorb ONCs at concentrations in the range of parts per million, and that we can effectively offset the concentration of ONC in the range of parts per billion on the downstream catalyst. The hydrocarbon feed stream may contain water up to and beyond saturation conditions. The hydrocarbon feed stream containing ONCs and water may be an aromatic feed stream, preferably including benzene, and suitably mainly benzene. As it flows through the adsorbent bed, the aromatic feed stream typically includes no more than 10% by weight of olefins. ONCs generally include a large proportion of basic ONCs, such as: indole, pyridine, quinoline, monoethanolamine (DEA), morpholine, including N-fluorenyl_morpholine (NFM) and N -Fluorenyl-tetrahydropyrrolidone (NMp). ONCs & may include a smaller proportion of weakly basic nitriles, such as acetonitrile, propionitrile, acrylonitrile, and mixtures thereof. The basic ONCs are well adsorbed by conventional clay or resin. 98299.doc -10- 200533651

附劑保護床。烴進料流被淮料I I進枓到習用的不純物吸附區域, 以吸附驗性ONCs及其他不站私 他+、、屯物,並且提供一個經處理之 缺乏驗性〇NCs的吸附流屮、、六 y 订級出級。我們發現:如:腈類之弱 驗性ONCs不良好吸附在翌田AA〜^ I仃隹白用的樹脂及黏土吸附劑上。腈Adhesive protection bed. The hydrocarbon feed stream is pumped into the customary impurity adsorption area by Huai Material II to adsorb sensible ONCs and other non-proprietary substances, and to provide a treated adsorption stream that lacks sensible ONCs, , Six y graded out of grade. We found that: for example, weak nitric acid-based ONCs do not adsorb well on the resins and clay adsorbents for Putian AA ~ ^ I 仃 隹 white. Nitrile

類通過習用的吸附劑床,允B d木並且可負面地影響下游製程, 如:烷化或轉烷化反應區域。 用來移除鹼性ONCs之黏土吸附劑包括由蘇化學 (sudchemie)提供的黏土,如:sc 63〇g、% 63犯及較佳 的SC 626GS。由費拓公司(Filtr〇1 c〇rp )提供的F_24黏土也 為適當。用來移除鹼性〇NCs之樹脂吸附劑包括由安博利 絲特(Amberlyst)線的樹脂,A_15為較佳,及可自羅門哈斯 公司(Rohm & Haas Company)獲得;和如:由普羅萊特有 限股份有限公司(Purolite International Limited.)提供的 CT- 1 75樹脂。其他種類的黏土及樹脂吸附劑為適當的。黏土 或樹脂吸附劑可在足以保持芳香流至少一部份在液相中的 條件下使用。周圍溫度高至38。〇(1〇〇卞)及壓力高於氣壓高 至206千巴斯卡(kPa)(每磅30平方吋)為足夠的。黏土及樹 脂能力範圍一般是在6及10重量。/。之胺及丨及2重量%2NFM 及NMP之間,是相對於吸附劑的重量。然而,在這些條件 下’黏土及樹脂較佳地吸附水及NFM及NMP,超過腈類。 因此,必須採用其他方式來吸附腈類。 適用於移除弱驗性ONCs的本發明吸附劑包括酸性分子 篩,如不同形式的矽鋁磷酸鹽及鋁磷酸鹽,揭示於美國專 利US 4,440,871、美國專利US 4,310,440及美國專利us 98299.doc 200533651 4,567,029 ;和沸石分子餘 ,,, 刀卞師。如在此所用,術語”分子篩”被 定義為一類吸附乾燥劑,直焱 ⑴具為天然鬲度結晶的,有定義為 微孔性或隧道的結晶神、^ ' 與丫-氧化銘的物質區分。在此類 結晶吸附劑的較佳種_八2 ^ & ' 禋頦刀子師為鋁矽酸鹽物質,一般已知 為濟石類。術語”彿石”―般指一群天然發生及合成的水合 金屬鋁矽酸鹽’其許多在結構上為結晶的。燒結形式的沸 石分子篩以下列通式代表:Similar to conventional adsorbent beds, it allows B d wood and can negatively affect downstream processes, such as alkylation or transalkylation reaction zones. Clay sorbents used to remove alkaline ONCs include clays provided by sudchemie, such as: sc 630 g,% 63 and preferably SC 626GS. F_24 clay provided by Filtrórcórp is also suitable. Resin adsorbents used to remove basic ONCs include resins from Amberlyst line, A-15 is preferred, and are available from Rohm & Haas Company; and such as: CT-1 75 resin supplied by Purolite International Limited. Other types of clay and resin adsorbents are suitable. Clay or resin sorbents can be used under conditions sufficient to maintain at least a portion of the aroma stream in the liquid phase. The ambient temperature is as high as 38. 〇 (100〇 卞) and pressure above atmospheric pressure up to 206 kilopascals (kPa) (30 square inches per pound) are sufficient. Clay and resin capacities are generally in the 6 and 10 weight range. /. The amine and the 2% by weight of 2NFM and NMP are relative to the weight of the adsorbent. However, under these conditions, 'clays and resins better adsorb water and NFM and NMP than nitriles. Therefore, other methods must be used to adsorb nitriles. The adsorbents of the present invention suitable for removing weakly sensible ONCs include acidic molecular sieves, such as different forms of silicoaluminophosphates and aluminophosphates, which are disclosed in US Patent No. 4,440,871, US Patent No. 4,310,440, and US Patent No. 98299.doc 200533651 4,567,029 ; And zeolite molecule I ,,, Dao Shi division. As used herein, the term "molecular sieve" is defined as a type of adsorption desiccant, which is naturally crystalline and has a crystallinity defined as microporosity or tunneling. It is distinguished from ^ -oxidized substances . The preferred species of this type of crystalline adsorbent is the aluminosilicate material, which is generally known as the jewel type. The term "fossil" generally refers to a group of naturally occurring and synthetic hydrated metal aluminosilicates, many of which are crystalline in structure. Zeolite molecular sieves in sintered form are represented by the following formula:

Me2/n〇 : a12〇3 : xSi〇2 : yH2〇 其中Me為陽離子、x具有從2到無限的值,n為陽離子價數 並且y具有從2到ίο的值。可#用的如外*、油 ^ 、 j 1更用的一般熱知沸石包括菱沸 石,也稱為沸石D;斜發沸石、毛沸石、八面沸石、沸石 β /弗石ω、彿石X、彿石γ、_沸石、沸石 (m)、鎂鹼沸石、絲光沸石、沸石A及沸石p。上面所 提之一些沸石的詳細敘述可發現於D_ w.布雷克(Back), 沸石分子篩(ZEOUTE職ECULAR SIEVES),紐約的約Me2 / n〇: a12〇3: xSi〇2: yH2〇 where Me is a cation, x has a value from 2 to infinity, n is a cation valence, and y has a value from 2 to ο. The commonly used thermal zeolites that can be used are as follows: *, oil ^, j 1 and more commonly include chabazite, also known as zeolite D; clinoptilolite, erionite, faujasite, zeolite β / Frzeite, omega X, fossil γ, _ zeolite, zeolite (m), ferrierite, mordenite, zeolite A and zeolite p. Detailed descriptions of some of the zeolites mentioned above can be found in D. W. Back, Zeolite Molecular Sieves, New York.

翰威力及兒子們(J0hn Wiley and s〇ns,New γ〇^),MM 中o 在化學組合物、結晶結構及如:χ_光粉末繞射型態之物 理,質中’不同合成及天然物質之間存在重大的不同。分 子師發生為微細結晶的凝結物、或合成為微細粉末,並且 較佳成藥片狀或錠狀做大規模吸附使用。成錠的方法為已 知’其不論是關於選擇性及能力,是非常令人滿意的,因 為分:篩的吸收特性基本上維持不變”交佳的吸附劑包括 具有氧化鋁或氧化矽黏合劑的沸石γ及沸石χ及具有氧化 98299.doc 200533651 鋁或氧化矽黏合劑的β沸石。沸石γ為最佳。 人具體實施例中,分子篩通常與耐火無機氧化物黏 使'。黏合劑可包括氧魅或氧切,而前者為 :土,亚且γ-乳化紹、η_氧化銘及其混合物為特佳。分子 師^存在的⑽圍是從5至99重量%的吸附冑,並且耐火無 機氧化物可存在的範圍是從1至95重量。/”在一個: 施例::分子筛可存在的份量是至少5。重量%的:二 並且較佳份量是至少7〇重量%的吸附劑。 、在本發明之吸附劑的分子篩為酸性的。使用矽對鋁比率 :對酸性程度的規格’在—個具體實施例中,料銘的比 “义』不夕於1GG,並且在另—個具體實施例中是不多於 25。在分子筛上的陽離子是不理想的。因此,在沸石叫 /弗石的m,酸洗對移除如:納之驗性金屬為理想的, 以顯出更多酸位置,因而增加吸附能力。矛多出骨架到黏合 劑的銘也必須被避免’因此其減少酸性。加人—些份量之 如驗土金屬及稀土金屬元素的陽離子到沸石X4Y,會改 $骨架鋁的熱及水熱穩定性,減少骨架鋁移出骨架的份 量。陽離子的加入份量必須足以低到避免抑制吸附表現。 本發明之分子篩吸附劑可具有與在下游反應器中之烧化觸 媒相同的組合物’該反應器如:烷化或轉烷化單元。然 而’當烧化觸媒比分子篩吸附劑更昂貴時,烧化觸媒的組 合物與分子篩較佳為不同的。 如所指出的’水的存在負面影響室溫下在酸性分子篩上 的& ^吸附。在表面上’出現的是:將到分子筛保護床之 98299.doc 200533651 進料中的水份減至最少是有益的。水份〇NCs競爭吸附位 置,因而減少分子篩對ONCs的能力。我們確定:在較低 溫下,水比腈類更佳地吸附在酸性分子篩上。然而,我們 進一步發現:在不過量濃度之水的存在下,在較高溫下酸 性分子篩吸附更面濃度的腈類。雖然不願受限於任何特別 的理卿,我們相佗·腈類是不夠驗性到吸附到酸性分子篩 吸附劑上。然後,在水的存在下,腈類在酸性分子筛上催 化性地水解成成醯胺類或胺類。然後鹼性醯胺類或胺類被 吸附到酸性分子篩上。 經污染、要純化腊類的烴進料流,必須在水的存在下、 升溫下流經酸性分子篩的吸附區域,在一個具體實施例中 為至少12CTC且不高於3〇(TC,在另一個具體實施例中該範 圍是大於125 C且不高於300。(:,並且在另一個具體實施例 中該範圍是大於150°C且不高於2〇〇。〇。在吸附劑床的壓力 必須在34·5千巴斯卡至4136 9千巴斯卡(絕對)(每磅5至6〇〇 平方吋)的範圍内。在需要再生之前,在分子篩吸附劑上 的ONC負載達到從〇.6至1〇重量%。在黏土吸附劑上的 〇NC負載是從丨.5至6 〇重量%,並且在樹脂吸附劑上的 〇NC負載是黏土的兩倍。因為樹脂或黏土吸附劑對於 ONCs具有較大的吸附能力並且較便宜,在其傳送到酸性 分子篩保護床以移除腈類之前,不純的烴流流經習用的黏 土或樹脂保護床,以移除鹼性的ONCs。然而,該酸性分 子篩保護床會吸附鹼性〇NCs,其自習用吸附劑床殘留。 較佳的是裝置酸性分子篩吸附劑床在下游與習用吸附劑床 98299.doc -14- 200533651 流通。因此,至少一部份來自習用吸附劑床的流出流必須 終將進料到酸性分子薛吸附劑床。再者,因為來自習用吸 附劑床之流出流的溫度可為周圍溫度,熱交換器可置於下 游與習用吸附劑床流通及上游與熱吸附劑床流通,以調整 適於熱吸附劑床的溫度。因而,至少_部份來自f用㈣ 劑床的流出流會在熱交換器中被加熱或冷卻,並且至少— 部份來自熱交換器的流出流會被進絡到熱吸附劑床。在_ 個具體實施例中,在其被進料到烷化及/或轉烷化反應區 域之前,所有的院化基質流必須在熱吸附劑床上脫氮。 當在分子篩保護床上時,煙進料流中的水濃度必須是在 20 wPPm至500 wppm之間,並且較佳是在5〇评卯爪至15〇 WPPm之間。在-個具體實施財,水濃度必須與腊轉化 成酸胺類或胺類相關的化學計量。 我們也發現:在分子㈣護床中存在水,減少在升溫下 吸附劑上的焦炭形成。在分子筛酸位置的焦炭累積做為阻 礙ONCs的吸附’造成再生之間的較短週期 '然而,藉著 減輕在酸位置上的焦炭形成,分子筛保護床可在再生之後 維持較長的,並在多週期操作時維持最大吸附能力, 因為各再生週期需要少掉許多的嚴格性。 當失效時’習用之黏土或樹絲護床不能再生。然而, 失效的黏土或m須被丢棄。本發明之失效分子薛可被 再生。分子篩保護床可包含—或多個固定床的分子筛。當 達到投產之分子篩吸附床的容量時,也就是較佳在絕大部 份之ONCs通過投產之分子篩吸附床之前,進料流被導向 98299.doc 15 200533651 在吸附區域中的備用分子篩吸附床。然後,前者的投產吸 附床以將内含物通過分餾區域而被排水。否則在吸附床的 再生期間’製程被停止。該吸附床可以熱天然氣流再生, 或藉著妷燒來燃燒來自分子篩的ONCs,或藉著任何其他 習用方法。然後,再生吸附床被置於備用,直到達到投產 的吸附床容量。 在精著烯烴烷化劑、以酸性觸媒催化而將芳香族的選擇 性烷化當中,烯烴可包含從2到至少20個碳原子,並且可 $有刀支或直線烯烴、終端或内烯烴。因此,該烯烴的特 疋天性不特別重要。院化反應所共同分享的是反應在至少 ^伤液相條件下進行,對低碳成員是藉著調整反應屡力而 容易達到的標準。在低碳稀烴當中,乙稀及丙稀是最重要 代表性的。包含烧化劑之烯烴進料流可包括乙稀及/或丙 烯。包括丙烯之烯烴進料流會是至少65重量%純的,以包 b例的丙院平衡’有—些重量%進料會超過Μ重量% 輕。乙烯進料-般是超過99重量%為純。在所餘之稀煙 虽中,清潔劑範圍烯烴之類是特別有興趣的。此類由含有 =°:。籍:直線稀煙所組成,其具有内部或終端 、主二二3有仗8至16個碳原子的直線烯烴是特別用做 圍烯烴,並且含有從1〇至14個碳原子的那些是特 仏做為清潔劑範圍稀煙。、 份提供於轉烧化反應區域。一 1°/乂夕烧基苯之燒基組 ...e , 一乙基本、三乙基苯及二異丙 土 ::夕烷基苯的重要實例,其可提供此類烧化劑。 本疋至今可烧化芳香族化合物的最重要代表,其可在本 98299.doc 200533651 發明之實施中用做烧化基質。芳香進料流可包含從5至 9”莫耳%的苯’並且可為來自苯乙稀單體生產工廉的回 收流。更-般地’芳香族化合物可選自由苯、冑、貧、菲 及其經取代之衍生物所構成的族群。在芳香族化合物上發 現之最重要類型的取代基為含有從碳原子的院基 分子團。另-個重要的取代基是經基分子團、及其烧基也 含有從U20個碳原子的院氧基分子團。其中取代基為燒 基或烧氧基,在石虫鼠鏈上苯基分子團也可被取代。雖然未 、二取代及單取代苯、奈、恩及菲是最通常用於本發明的實 施中,也可使用多取代芳香族。除了上述的那些,適當之 可烷化芳香族化合物的實例包括聯苯、甲苯、二甲苯、乙 基苯、丙基苯、丁基苯、戊基苯、己基苯、庚基苯、辛基 苯等等。 廣泛種類的觸媒可用於烧化反應區域。用於該反應區域 的適當觸媒可包括不遭受水存在之有害影響的任何觸媒。 較佳地,錢化觸媒的存在下,大量的水可被忍受或要 ^大量的水較佳地意為在進入燒化區域之反應物中的水 浪度是至少50 wppm。該烧化反應區域可具有水含量少如 2夕〇 wPpm、到超過2〇〇 wppm,並且高至麵那㈣或更 ^用方、本t明之車父佳觸媒是沸石觸媒。本發明之觸媒通 吊與耐=無機氧化物黏合劑組合使用。較佳的黏合劑為氧 化銘或乳化硬。適當的沸石包括沸石β、MM]、㈣小 2 MCM_36、MCM-49、及批156。沸石 β被敘述 吴國專利US 5,723,71〇中。較佳的院化觸媒是具有氧化 98299.doc 200533651 紹或氧化矽黏合劑的¥類彿石、或具有氧化紹或氧化矽黏 合劑的β沸石。沸石存在的份量是至少5〇重量%的觸媒, 並且更佳的份量是至少7()重量%的觸媒。 在烧化反應進行之下的特別條件,取決於所狀芳香族 :匕口物及烯。因為反應在至少部份為液相的條件下進 反應壓力被調整到維持該稀烴至少部份為液相。對高 碳稀烴而t,該反應可在自生壓力下進行。壓力可在101 千巴斯卡至1 3 1 72千巴斯卡的廣泛範圍中變化。為務實情 況’壓力-般是在1379千巴斯卡及6985千巴斯卡(每碌綱 至1〇00平方叫^之間的範圍,但是通常是在2069及4137千 巴斯卡(每石旁300至_平方对)之間的範圍。但是我們再次 強調:壓力不是關鍵變數,並且只需要^以維持至少部份 為液相的條件。代表性㈣化温度包括飞乙敎化苯在 170 C及250 C之間的範圍,並且以丙烯烷化苯在90。。及 _之間的範圍。適於以C2至Cm範圍烯烴烧化本發明之 可烷化芳香族化合物的溫度範圍,是在60°C及400它之 $,最通常的溫度範圍是在9〇t&25〇t:之間。反應物通 吊以足以產生液體小時空間速度從〇 2至5〇小時·〗的質量流 速通過烷化區域,並且特別是從〇5至1〇小時4。 ^用於本發明方法中之可烷化芳香族化合物對烯烴的比 率會取決於所要之選擇性烷化的程度、及反應混合物中 芳香族和烯烴組份的相對成本。對以丙烯烷化苯而言, 笨對-烯烴的比率可低為15,並且高為1〇〇,以至8.0 的比率較佳。當苯以乙烯烷化時,苯_對_烯烴的比率是在 98299.doc -18- 200533651 2:1及8:1之間較佳。對C6至Cm的清潔劑範圍烯烴而言,在 5 :1至咼如30:1之間的苯_對_烯烴比率通常是足以確保所要 的烧化選擇性’而在8:1及2G:1之間的範圍、甚至更高為理 想的。 在有苯烷化基質及丙烯烷化劑的異丙苯生產中,含丙烯 物流一般也包含丙烷。該丙烯物流可包含從〇至5〇重量% 丙烷,並且一般該丙烯物流可包含從〇 5至35重量%丙烷。 烷化反應區域通常會提供廣泛種類的不想要副產物。例 如·以乙稀烧化笨,產生乙基苯,除了其他乙稀縮合產物 之外,該反應區域也可產生二-及三乙基苯。類似地,以 丙烯烷化苯,產生異丙苯,除了仍更多的縮合產物之外, 該反應區$可產生二·及三異丙基苯。纟㈣化反應器 中’這些多烧化芳香族接觸額外的芳香基f,產生額外的 單:^化產物本舍明之轉烧化反應區域會使用沸石觸媒。 該沸石存在的份量是至少50重量%的觸媒,並且較佳份量 是至少90重量%的觸媒。在大部份情況下,該沸石觸媒再 包括無機氧化物黏合劑。用於轉烷化觸媒之較佳無機氧化 物是氧化鋁,以γ-氧化鋁、η —氧化鋁及其混合物為特佳。 該沸石存在的範圍是從5至99重量%的觸媒,並且耐火無 機氧化物黏合劑可存在的範圍是從1至95重量%。較佳的 轉烷化觸媒是具有氧化鋁或氧化矽黏合劑的沸石γ、或具 有氧化鋁或氧化矽黏合劑的β沸石。 烷化反應區域及轉烷化反應區域不需要使用相同的觸 媒。此製程被用於烷化反應區域及轉烷化反應的任何排 98299.doc -19- 200533651 置。然:,已發現:當用於垸化反應區域及轉燒化反應區 或兩者T包合於氧化鋁黏合劑中之β沸石或高Υ類型沸石 έ非#良好地表現。因此,在本發明的一個具體實施例 中’在異丙苯内容物中,兩個反應區域會使用相同的觸 媒· β沸石。反而在乙基苯的情況下,烷化及轉烷化反應 區域會較佳地分別使用β沸石及Υ-類型沸石。另外,在烷 化反C區域中發生轉烧化反應’並且在轉烧化反應區域中 赍生込化反應,兩個區域可被稱為烷化區域。 可為理想的是使用烷化區域或轉烷化區域的第一床,其 使用酸性分子篩觸媒作為吸附劑區域,用來移除腈類。在 此情況下,吸附劑及觸媒必須在空間上間隔。烷化劑必須 繞過吸附區域,並且被傳送到床間層的空間中,與存在於 吸附區域的脫氮烷化基質混合。然而,較佳的是在分別容 器中包含熱吸附區域及烷化區域。 轉烷化反應可在廣泛範圍的操作條件下進行,其包括溫 度從100 C至390°c (212°F至734°F)、並且壓力範圍是從101 至13171千巴斯卡(每磅14·7至1910平方吋)。再者,壓力通 蓽被遥擇使得反應物維持在液相中。因此,轉烷化反應區 域中的較佳壓力範圍是從1013至5066千巴斯卡(每磅147至 734平方吋)。液體小時空間速度從〇.2至5〇小時-〗對轉烷化 反應區域為理想,LHSV從0.5至50小時-1為較佳。 轉烧化及烧化反應區域可能任何方式操作及排置,其提 供所要的操作溫度及接觸階段的數量。在烧化區域中之多 重接觸階段疋彳貝用的,藉著階段添加反應物到烧化觸媒的 98299.doc -20- 200533651John Willy and his sons (J0hn Wiley and soens, New γ〇 ^), MM o in the chemical composition, crystal structure and physics such as: χ_ light powder diffraction pattern in the 'different synthesis and nature There are major differences between substances. The molecular division occurs as a finely crystalline agglomerate, or is synthesized into a fine powder, and is preferably used in the form of tablets or tablets for large-scale adsorption. The method of forming ingots is known 'It is very satisfactory, both in terms of selectivity and capacity, because the absorption characteristics of the sieve remain essentially unchanged.' Zeolite γ and zeolite χ and β zeolite with an oxide 98299.doc 200533651 aluminum or silica binder. Zeolite γ is the best. In specific embodiments, molecular sieves are usually bonded with refractory inorganic oxides. The binder can be Including oxygen charm or oxygen cutting, the former is: soil, sub-γ-emulsification, η-oxidation, and mixtures thereof are particularly preferred. The range of the molecular division ^ is from 5 to 99% by weight of adsorption tritium, and Refractory inorganic oxides can be present in a range from 1 to 95 weights. / "In one: Example: The molecular sieve can be present in an amount of at least 5. % By weight: two and the preferred amount is at least 70% by weight of the adsorbent. The molecular sieve in the adsorbent of the present invention is acidic. Use of silicon to aluminum ratio: the specification of the degree of acidity 'in one embodiment, the ratio of the material name is not less than 1GG, and in another embodiment is not more than 25. On molecular sieves The cations are not ideal. Therefore, at the zeolite / Furst m, pickling is ideal for removing metals such as sodium to show more acid sites and thus increase the adsorption capacity. The skeleton-to-binder inscription must also be avoided 'so it reduces acidity. Adding people—some amounts of cations such as earth metal and rare earth metal elements to zeolite X4Y will change the thermal and hydrothermal stability of the framework aluminum, reducing The amount of framework aluminum removed from the framework. The amount of cations added must be low enough to avoid inhibiting adsorption performance. The molecular sieve adsorbent of the present invention may have the same composition as the calcination catalyst in the downstream reactor. Or transalkylation unit. However, when the calcination catalyst is more expensive than the molecular sieve adsorbent, the composition of the calcination catalyst is preferably different from the molecular sieve. As noted, the presence of water negatively affects the room temperature at room temperature. &Amp; ^ Adsorption on the molecular sieve. What appears on the surface: It is beneficial to minimize the water in the feed to the molecular sieve protection bed 98299.doc 200533651. The water NCs compete for the adsorption site, thus reducing The ability of molecular sieves to ONCs. We determined that at lower temperatures, water adsorbs better on acidic molecular sieves than nitriles. However, we further found that in the presence of excessive concentrations of water, acidic molecular sieves adsorbed at higher temperatures More concentrated nitriles. Although we do not want to be limited by any special reason, we are not aware that nitriles are not sufficiently susceptible to adsorption on acidic molecular sieve adsorbents. Then, in the presence of water, nitriles are acidic. The molecular sieves are catalytically hydrolyzed into ammonium amines or amines. The basic ammonium amines or amines are then adsorbed onto the acidic molecular sieve. The contaminated hydrocarbon feed stream to purify the waxes must be in the presence of water 3. The adsorption area flowing through the acidic molecular sieve under elevated temperature is at least 12CTC and not higher than 30 ° C in one specific embodiment. In another specific embodiment, the range is greater than 125C and not higher than 300C. (And, in another specific embodiment, the range is greater than 150 ° C and not higher than 2000. The pressure in the adsorbent bed must be between 34.5 kPa and 4136 kPa (Absolute) (5 to 600 square inches per pound). Before regeneration is required, the ONC load on the molecular sieve adsorbent reaches from 0.6 to 10% by weight. On the clay adsorbent, 0NC The load is from 1.5 to 60% by weight, and the 0NC load on the resin adsorbent is twice that of clay. Because the resin or clay adsorbent has a larger adsorption capacity for ONCs and is cheaper, it is delivered to Before the acidic molecular sieve protection bed removes nitriles, impure hydrocarbon streams flow through the conventional clay or resin protection bed to remove alkaline ONCs. However, the acidic molecular sieve protection bed will adsorb alkaline ONCs. Adsorbent bed remains. It is preferred that the device has an acidic molecular sieve adsorbent bed that circulates downstream with the conventional adsorbent bed 98299.doc -14-200533651. Therefore, at least a portion of the effluent from the conventional adsorbent bed must eventually be fed to the acidic molecular adsorbent bed. Furthermore, because the temperature of the outflow from the conventional adsorbent bed can be the ambient temperature, the heat exchanger can be placed downstream to communicate with the conventional adsorbent bed and upstream to communicate with the thermal adsorbent bed to adjust the temperature suitable for the thermal adsorbent bed. temperature. Thus, at least part of the effluent flow from the ㈣ agent bed will be heated or cooled in the heat exchanger, and at least part of the effluent flow from the heat exchanger will be entrained into the thermal adsorbent bed. In one particular embodiment, all of the institutionalized matrix stream must be denitrified on a thermal adsorbent bed before it is fed into the alkylation and / or transalkylation reaction zone. When on a molecular sieve guard bed, the water concentration in the smoke feed stream must be between 20 wPPm and 500 wppm, and preferably between 50 and 150 WPPm. In one implementation, the water concentration must be related to the stoichiometry of the conversion of wax to acid amines or amines. We have also found that the presence of water in the molecular tritium bed reduces the formation of coke on the adsorbent at elevated temperatures. The accumulation of coke at the acid position of the molecular sieve acts as a barrier to the adsorption of ONCs 'causing a shorter cycle between regenerations'. However, by reducing coke formation at the acid position, the molecular sieve protection bed can be maintained longer after regeneration and Maximum adsorption capacity is maintained during multi-cycle operation, since each regeneration cycle requires much less stringency. When it fails, the conventional clay or silk guard beds cannot be regenerated. However, the failed clay or m must be discarded. The ineffective molecule Xue of the present invention can be regenerated. The molecular sieve protection bed may include—or multiple fixed bed molecular sieves. When the capacity of the molecular sieve adsorption bed in operation is reached, that is, preferably before the majority of the ONCs pass through the molecular sieve adsorption bed in operation, the feed stream is directed to a spare molecular sieve adsorption bed in the adsorption zone. The former then puts the adsorbent bed into operation to drain the contents through the fractionation zone. Otherwise, the process is stopped during regeneration of the adsorption bed. The adsorbent bed can be regenerated by a hot natural gas stream, or burned ONCs from molecular sieves by sintering, or by any other conventional method. The regenerated adsorbent bed is then placed on standby until it reaches the capacity of the adsorbent bed in production. In the selective alkylation of aromatics with refined olefin alkylating agents and acidic catalysts, olefins can contain from 2 to at least 20 carbon atoms, and can be knife or linear olefins, terminal or internal olefins. . Therefore, the nature of the olefin is not particularly important. The common reaction of the hospitalization reaction is that the reaction is performed under the condition of at least liquid phase, which is a standard that can be easily reached for low-carbon members by adjusting the reaction time and again. Among the low-carbon dilute hydrocarbons, ethylene and propylene are the most important representatives. The olefin feed stream comprising the burner may include ethylene and / or propylene. The olefin-containing feed stream including propylene will be at least 65% by weight pure, and some of the weight% feed will exceed M% by weight. Ethylene feed-generally more than 99% by weight is pure. Of the remaining thin fumes though, detergent range olefins and the like are of particular interest. This class contains = ° :. The linear olefins are composed of linear thin smoke, which have internal or terminal, main 223, and 8 to 16 carbon atoms. The linear olefins are especially used as enc olefins, and those containing from 10 to 14 carbon atoms are special仏 Thin smoke as a cleaning agent. , Serving is provided in the transfusing reaction area. -1 ° / Cyclosylbenzene group ... e, monoethylbenzyl, triethylbenzene, and diisopropyl clay: important examples of alkylbenzene, which can provide such a calcining agent. The present invention is by far the most important representative of aromatic compounds that can be burned, which can be used as the burning matrix in the implementation of the invention of 98299.doc 200533651. The aromatic feed stream can contain from 5 to 9 "mole% of benzene 'and can be a recycle stream from the production of styrene monomer. More generally, aromatic compounds can be selected from free benzene, amidine, lean, The group consisting of phenanthrene and its substituted derivatives. The most important type of substituents found on aromatic compounds are radicals containing carbon atoms. Another important substituent is via radicals, Its alkyl group also contains a group of oxygen radicals from U20 carbon atoms. Among them, the substituent is alkyl or alkoxy, and the phenyl group can be substituted on the stoneworm chain. Although unsubstituted, disubstituted and Mono-substituted benzene, naphthalene, phen, and phenanthrene are the most commonly used in the practice of the present invention, and poly-substituted aromatics can also be used. In addition to those described above, examples of suitable alkylatable aromatic compounds include biphenyl, toluene, diphenyl Toluene, ethylbenzene, propylbenzene, butylbenzene, pentylbenzene, hexylbenzene, heptylbenzene, octylbenzene, etc. A wide variety of catalysts can be used to burn the reaction zone. Suitable catalysts for this reaction zone The media can include any Catalyst. Preferably, a large amount of water can be tolerated or required in the presence of a coin catalyst. A large amount of water is preferably meant to be at least 50 wppm in the reactants entering the burning zone. The calcination reaction area may have a water content as low as 2 wPpm, to more than 200 wppm, and as high as noodles or more, the Chevrolet catalyst of the present invention is a zeolite catalyst. The catalyst is used in combination with a resistant = inorganic oxide binder. The preferred binder is oxidized or emulsified hard. Suitable zeolites include zeolite β, MM], ㈣ 2 MCM_36, MCM-49, and batch 156. Zeolite β is described in Wu Guo patent US 5,723,71. The preferred chemical catalyst is a ¥ fossil with an oxidation 98299.doc 200533651 or a silica adhesive, or an oxide with a silica or a silica adhesive. Beta zeolite. Zeolite is present in an amount of at least 50% by weight of the catalyst, and more preferably in an amount of at least 7 (%) by weight of the catalyst. The special conditions under which the calcination reaction proceeds depend on the aromatic being present: Daggers and olefins, because the reaction proceeds under the condition that at least part of the liquid phase The force is adjusted to maintain the dilute hydrocarbon at least partially in the liquid phase. For high-carbon dilute hydrocarbons, the reaction can be carried out under autogenous pressure. The pressure can be between 101 kPa and 1 3 1 72 kPa. Variations in a wide range. For pragmatic situations, the pressure is generally between 1379 kilopascals and 6985 kilopascals (per square to 10000 squares, but usually between 2069 and 4137 kilobars). Range between 300 to _ square pairs per stone. But we stress again: pressure is not a critical variable and only ^ is required to maintain at least part of the liquid phase condition. Representative tritiated temperatures include Fei Tritiated benzenes range between 170 C and 250 C, and propylene alkylated benzenes range between 90 ° and _. The temperature range suitable for the calcination of the alkylizable aromatic compounds of the present invention in the range of C2 to Cm is between 60 ° C and 400 ° C. The most common temperature range is between 90 ° and 250 °: . The reactants hang through the alkylation zone at a mass flow rate sufficient to produce a liquid hourly space velocity from 02 to 50 hours, and particularly from 05 to 10 hours4. ^ The ratio of alkylable aromatic compounds to olefins used in the process of the present invention will depend on the degree of selective alkylation desired and the relative costs of the aromatic and olefin components in the reaction mixture. For alkylating benzene with propylene, the ratio of stupid to olefin can be as low as 15 and as high as 100, and a ratio of up to 8.0 is preferred. When benzene is alkylated with ethylene, the benzene-to-olefin ratio is preferably between 98299.doc -18- 200533651 2: 1 and 8: 1. For cleaners ranging from C6 to Cm, benzene-to-olefin ratios between 5: 1 and 30: 1 are usually sufficient to ensure the desired burn selectivity ', while at 8: 1 and 2G: 1 The range is even higher. In the production of cumene with a benzene alkylation matrix and a propylene alkylating agent, propylene-containing streams also typically include propane. The propylene stream may contain from 0 to 50% by weight propane, and in general the propylene stream may contain from 5 to 35% by weight propane. The alkylation reaction zone typically provides a wide variety of unwanted by-products. For example, • Ethylene is burnt to produce ethylbenzene. In addition to other ethylene condensation products, di- and triethylbenzene can also be produced in this reaction zone. Similarly, benzene is alkylated with propylene to produce cumene. In addition to still more condensation products, this reaction zone $ can produce di- and tricumyl. These multi-burned aromatics in the tritiation reactor are exposed to additional aromatic groups f to generate additional monomers: The zeolite catalyst is used in the trans-sintering reaction zone of the benminite. The zeolite is present in an amount of at least 50% by weight of the catalyst, and a preferred amount is at least 90% by weight of the catalyst. In most cases, the zeolite catalyst further includes an inorganic oxide binder. The preferred inorganic oxide for the transalkylation catalyst is alumina, with γ-alumina, η-alumina and mixtures thereof being particularly preferred. The zeolite is present in the range of 5 to 99% by weight of the catalyst, and the refractory inorganic oxide binder may be present in the range of 1 to 95% by weight. Preferred transalkylation catalysts are zeolite gamma with alumina or silica binder, or beta zeolite with alumina or silica binder. It is not necessary to use the same catalyst for the alkylation reaction zone and the transalkylation reaction zone. This process is used in the alkylation reaction zone and in any row of the transalkylation reaction 98299.doc -19- 200533651. However, it has been found that when used in the tritiation reaction zone and the transfiring reaction zone, or both, the β zeolite or high zeolite type zeolite which is contained in the alumina binder performs well. Therefore, in a specific embodiment of the present invention, 'in the cumene content, the same catalyst · beta zeolite is used in the two reaction regions. On the contrary, in the case of ethylbenzene, it is preferable to use beta zeolite and rhenium-type zeolite in the alkylation and transalkylation reaction regions, respectively. In addition, transalkylation reaction 'occurs in the alkylation trans-C region and a tritiated reaction is generated in the transalkylation reaction region, and the two regions may be referred to as alkylation regions. It may be desirable to use a first bed of an alkylation zone or a transalkylation zone that uses an acidic molecular sieve catalyst as the adsorbent zone to remove nitriles. In this case, the sorbent and catalyst must be spaced apart. The alkylating agent must bypass the adsorption zone and be transported into the interbed space to be mixed with the denitrified alkylating matrix present in the adsorption zone. However, it is preferable to include a heat adsorption region and an alkylation region in separate containers. The transalkylation reaction can be performed under a wide range of operating conditions including temperatures from 100 C to 390 ° C (212 ° F to 734 ° F) and pressures ranging from 101 to 13171 kilobasca (14 per pound) 7 to 1910 square inches). Furthermore, the pressure pump is remotely selected so that the reactants are maintained in the liquid phase. Therefore, the preferred pressure range in the transalkylation reaction zone is from 1013 to 5066 kilopascals (147 to 734 square inches per pound). The hourly space velocity of the liquid from 0.2 to 50 hours-is ideal for the transalkylation reaction zone, and the LHSV is preferably from 0.5 to 50 hours-1. The transfiring and firing reaction zones may be operated and arranged in any way, which provides the desired operating temperature and number of contact stages. 98299.doc -20- 200533651 for the heavy contact stage in the calcination area, which is used for tadpoles in the calcination zone to add reactants to the calcination catalyst.

多重床來提供冷卻。反應物多重注入當做冷卻在烧化觸媒 床之間的階段,並且提供溫度控制。因此院化觸媒被安排 在多重床中,以容許床間層注入烧化劑。分別的烧化觸媒 床可安排在單一容器中或多重容器中。本發明可對烷化區 域及轉烧化區域使用傳統平行排置,其中進料流被獨立送 到各反應區域,並且流出物分開地被回收。另外,反應區 域可對來自轉炫化區域的流出流具有一系列流動安排^ 聯到有額外苯的烧化區域,或反之亦然。在烧化區域中, 大為過量的苯可通過一系列的烷化觸媒床,有中間階段注 入燒化劑及任何額外份量的苯。烧化反應器流出流的循環 也可優越地用來中止反應各別觸媒床,來進一步改進温度 控制’而不需要額外消耗新鮮的苯。在系列的流動= 中,一般容器可包含轉烧化反應區域及一或多個烧化反岸 區域。對非常大的單元而言’用於轉院化觸媒床及一或多 個烷化觸媒床的各別容器為更優越的。Multiple beds to provide cooling. Multiple injection of reactants acts as a cooling stage between the catalyst bed and provides temperature control. Therefore, the catalyst is arranged in a multiple bed to allow the bed to be injected with a calcining agent. Separate firing catalyst beds can be arranged in a single container or multiple containers. The present invention can use a conventional parallel arrangement for the alkylation zone and the trans-sintering zone, in which the feed stream is sent to each reaction zone independently, and the effluent is recovered separately. In addition, the reaction zone can have a series of flow arrangements for the effluent stream from the transamination zone to the calcination zone with additional benzene, or vice versa. In the calcination zone, a large excess of benzene can pass through a series of alkylation catalyst beds, with an intermediate stage injection of the calcining agent and any additional amounts of benzene. The circulation of the effluent stream from the calcination reactor can also be advantageously used to stop the respective catalyst beds to further improve the temperature control 'without the need for additional consumption of fresh benzene. In a series of flow =, a general vessel may include a trans-sintering reaction zone and one or more anti-shoaling zones. For very large units, the individual containers used for the transfer catalyst bed and one or more alkylation catalyst beds are more advantageous.

各別區域會被用來回收烷化產物。在分離區域中、至少 個以留i合上的頂部冷凝器,可被用來從塔頂流中分離出 ^ I且"卩伤的芳香烴冷凝物回到該塔做回流。從頂部 :除水疋困難的’由於水在苯中的高溶解度。然而,在苯 *中的些水加速腈類的移除。苯塔的頂部冷凝器可被操 作來減少水濃縮到· wppm份量。來自脫丙烧器塔的中間 體流可提供有水濃度5〇至150 wPpm的苯流。 I月方法及裝置之具體實施例的另外敘述,以參考所 附圖不呈現。该圖示代表本發明之具體實施例的觀點,並 98299.doc -21- 200533651 且不意欲為在本發明之一般廣泛範疇及所示請求項的限 制而要的疋·一些各式各樣的附屬物,包括閥門、泵、 分離裔、接收器、熱交換器等,從圖中排除。只有對清楚 及完全了解本發明之方法及裝置所需要的那些容器被說 明。在所有的情況下,該製程是一個連續製程。 圖1說明本發明的一個具體實施例,用於生產乙基苯。 含有乙烯之物流在管線14進入製程,並且分別被注入第一 及第二烷化反應器20、30。雖然轉烷化反應發生於烷化反 應器20、30,烷化反應為主要,烷化反應器被顯示為向上 流的反應器,但是向下流的反應器也為適當。乙烯在管線 14a-f中被注入烧化反應器2〇、3〇,在進入觸媒床2〇d_f、 30d-f之前,到床前置空間2〇a_c、3〇a-c。觸媒床2〇d_f、 30d-f包含烷化觸媒,以烷化苯及乙烯,產生乙基苯。在管 線10的苯被進料到第一烷化反應器20中,其中其起初與來 自管線14a的乙烯在床前置空間20a中混合,並且進入觸媒 床20d。來自觸媒床20d的流出流與自管線14b的新鮮乙稀 在床前置空間20b中混合,並且進入觸媒床2〇e。製程被重 覆在第一烷化反應器20中之床的數目。雖然三個觸媒床被 顯示器於烷化反應器20、30中,更多或更少可為適當的。 來自第一烷化反應器20之中間體烷化流出流,在管線丨8中 被運送到第二:):完化反應器30。在其運送到床前置空間3〇a 之前,熱交換器22冷卻在管線1 8中之流出流到所要的烧化 溫度。來自管線14d之注入床前置空間30a的乙稀,與來自 管線1 8中之中間體烷化流出流混合,並且進入觸媒床 98299.doc -22- 200533651 30d。相同的製程對觸媒床3〇e&3〇f重覆,並且來自第二 烷化反應器30的烷化反應器流出流在管線32中被運送到苯 之40 "亥火兀化反應為流出流可以通過未顯示之壓力控制閥 減壓,可以也未顯示之加熱器或熱交換器、或兩者加熱。 另外’更多或更少烷化反應器可為適當的。 若烷化反應器20、30及轉烷化反應器5〇如圖i顯示地為 平行運作,來自管線1〇的苯被按路徑、經由管線52送到轉 烧化反應态50。管線54從PEB塔90的頂部運載聚乙基苯 (PEB)塔頂流二乙基苯(DEB)及三乙基苯(teb),與在管線 52的笨混合,提供轉烷化進料管線58。轉烷化反應器刈包 含轉烷化觸媒的三個觸媒床50a-5〇c。可使用更多或更少 的觸媒床於轉烷化反應器5〇中。轉烷化觸媒促進轉烷化反 應,其中來自DEB及TEB的乙基基團以苯轉烷化,產生乙 基苯。因此,官線56比轉烷化進料管線58包含更大濃度的 乙基苯,並且較低濃度的DEB及TEB。 如圖1所示,烷化及轉烷化反應器為平行,三個不同物 ^被進料到苯塔40。在管線32中之烷化反應器流出流及在 吕線56中之轉烷化流出流,進料苯、乙基苯、及丁RE 和較重的PEBs到苯塔40中。在管線12中之新鮮進料苯流經 裝有黏土或樹脂吸附劑之床46的習用吸附劑容器料以吸附 雜貝,包含來自苯流之鹼性0NCs管線48將經純化之苯流 朮至笨i合4〇。經純化之苯流一般包含4〇〇至8〇〇卿仲]的 "本σ 40刀離進料成至少兩個物流。包含苯之苯塔塔頂 *、、二由官線62離開苯塔,並且進行冷凝器64,在其中其冷 98299.doc -23 · 200533651 卻到溫度在120°C及170°C之間。冷凝頂部進入接收器66, 其包括用來分散在管線66a中不溶解或游離之水、及若需 要之在管線66b中輕氣體的捕捉器。在管線68中、以包括 腈類之ONCs污染的頂部烴流,被運送到熱吸附劑容器 70,同時頂部烴流的一部份被回流到苯塔40中。頂部烴流 包括50至500 wppm的水。熱吸附劑容器70包含酸性分子篩 的熱吸附劑分子篩床72,其會在適當條件下吸附包括腈類 的ONCs。在管線68中之頂部烴流的溫度及水濃度是良好 地適於從烴流、以酸性分子篩選擇性吸附腈類。因此,在 管線10中之脫氮化的苯流,實際上不包含ONCs,其是不 多於30 wppb。包含產物乙基苯及包括PEBs之副產物的苯 塔塔底流,在管線74中離開苯塔,並且進入乙基苯塔80。 乙基苯塔80以蒸餾將來自管線74之苯塔塔底流分離成兩 個物流。包含產物乙基苯之乙基苯塔塔頂流在管線82中離 開乙基苯塔80,並且從製程中回收。乙基苯塔塔底流包含 副產物PEBs,一般包括DEBs、TEBs及較重的PEBs,如: 丁基苯類、二丁基苯類、三丁基苯類、乙基丁基苯類、二 乙基丁基苯類及二苯基乙烷。乙基苯塔塔底流在管線84中 離開乙基苯塔80,並且通過PEB塔90。 PEB塔90將在管線84中的乙基苯塔塔底流分離成兩個物 流。包含比TEB更重之PEBs的PEB塔塔底流,在管線92 中、從PEB塔90的底部離開,並且從製程中被拒絕。包含 DEBs及TEBs的PEB塔塔頂流在管線54中離開從PEB塔90, 並且如前述地回收,與在管線52中、到轉烷化反應器50的 98299.doc -24- 200533651 進料混合。 在圖!中的具體實施例使用兩個吸附劑床,當所有的貌 化基質可能被ONCs污染時,其合作從烧化基質進料移除 〇NCs。樹脂或黏土吸附劑⑽移除大量的ο·,同時熱 吸附劑分子篩床72吸附包括腈類的所餘嶋,其會毒化 焼化及轉烧化觸媒。 圖2顯示-個方法及裝置’其可在從如:苯乙烯單體單 元之另-個來源回收苯時優越地使用,該方法及裝置為用 於製造乙基苯之總苯的-個部份,並且來自其他來源之回 收苯可能被ONCs污染。在圖2中標示元件的所有參考數字 是相對應於圖!中的類似元件,但是具有不同型態會以單 运點符號(,)標示。否則,相同參考數字被定為在圖i及2 中、具有相同型態的相對應元件。另夕卜,雖㈣2顯示烧 化反應器及轉烷化反應器為平行,其可串聯操作。 在官線12'中的新鮮進料苯,流經包含樹脂或黏土吸附 劑床4 6的習用吸附劑容器4 4,從苯流吸附包括◦ n c s的不 純物。無腈類被預期在管線12,中的新鮮進料苯裡。經純化 的苯流一般包含400至800 wppm的水。管線48,運載經純化 的苯流’與在管線68,中的苯塔塔頂流組合1期包含赌類 之另一個來源的苯,在管線8中被運送到熱吸附劑容器 中。在管線8中之苯流從苯乙烯單體單元回收,並可包含 在50及800评卯爪之間的水,並且一般為水飽和的。熱吸附 劑容器70包含酸性分子篩的吸附床72,其在適當條件下吸 水需要被注 附包括腈類的ONCs。若水濃度低於50 wppm 98299.doc -25- 200533651 入笨流中。若水濃度高於5 〇 Wppm,優越的是乾燥苯流。若 在管線8中之苯流的溫度不是至少i2〇°C,並且較佳高於us 且不高於300°C,必須加熱或冷卻到適當的溫度。此溫度 範圍及水濃度是良好地適於從烴流、以酸性分子篩選擇性 吸附腈類,並且以吸附鹼性〇NCs。因此,在管線32中之 脫氮苯流實際上不包含〇NCs到偵測份量3〇 wppb,與在管 線48’中之經純化的苯流混合,並且在管線68,中之苯塔拔 頂流混合,提供在管線1 〇,中之不含氮苯流。 官線10’中之苯流送至烷基化反應器2〇、3〇並經由並行 之官線52’送至烷基轉移反應器5〇。在管線1〇,中之苯被運 送到烷化反應器20、30中,並且與管線14供應之乙烯、在 適當觸媒上反應,如關於圖丨所解釋的。在管線32中之烷 化流出流被運送到苯塔40中。在管線54,中之來自PEB塔頂 流的DEB及TEB,與在管線52,中之苯流混合,提供在管線 58中之轉烷化進料流,其被運送到轉烷化反應器5〇中。 DEB及TEB與苯在反應器50中的反應,相對於在管線“中 之轉烷化進料流,產生增加濃度的乙基苯、及在管線56中 之轉烷化流出流的DEB及TEB減少濃度。在管線56中之轉 燒化流出流被運送到苯塔4〇中。 笨塔40將進料分離成至少兩個物流。含苯之苯塔塔頂流 經由管線62離開苯塔,並且進入冷凝器64,在其中其冷卻 到溫度在120°C及170°C之間。冷凝頂部進入接收器66,其 匕括用來分散在管線66 a中不溶解之水、及若需要之在管 線66b中輕氣體的捕捉器。在管線68,中之包含大部份笨的 98299.doc -26- 200533651 頂部烴流,如前述地被回收到管線1〇|,同時頂部烴流的一 部份被回流到苯塔4时。包含產物乙基苯及包括pEBs之副 產物的苯塔塔底流,在管線74中離開苯塔,並且進入乙基 本塔8 0。Individual areas are used to recover the alkylation products. In the separation zone, at least the top condensers closed to leave can be used to separate the ^ I and " smelled aromatic hydrocarbon condensate from the overhead stream back to the column for reflux. From the top: It is difficult to remove water because of the high solubility of water in benzene. However, some water in benzene * accelerates the removal of nitriles. The top condenser of the benzene column can be operated to reduce water concentration to wppm. The intermediate stream from the depropanizer column can be supplied with a benzene stream having a water concentration of 50 to 150 wPpm. The detailed description of specific embodiments of the method and device in January will not be presented with reference to the accompanying drawings. This illustration represents a view of a specific embodiment of the present invention, and is 98299.doc -21-200533651 and is not intended to be essential in the general broad scope of the present invention and the limitations of the claimed items. Some various Attachments, including valves, pumps, separators, receivers, heat exchangers, etc., are excluded from the picture. Only those containers required for a clear and complete understanding of the method and apparatus of the present invention are described. In all cases, the process is a continuous process. Figure 1 illustrates a specific embodiment of the present invention for the production of ethylbenzene. The ethylene-containing stream enters the process in line 14 and is injected into the first and second alkylation reactors 20, 30, respectively. Although the transalkylation reaction occurs in the alkylation reactors 20 and 30, the alkylation reaction is the main, and the alkylation reactor is shown as an upstream reactor, but a downstream reactor is also suitable. Ethylene is injected into the calcination reactors 20 and 30 in lines 14a-f, and before entering the catalyst beds 20d_f and 30d-f, it goes to the bed front spaces 20a_c and 30a-c. The catalyst beds 20d_f and 30d-f contain alkylation catalysts to alkylate benzene and ethylene to produce ethylbenzene. Benzene on line 10 is fed into the first alkylation reactor 20, where it is initially mixed with ethylene from line 14a in the bed headspace 20a and enters the catalyst bed 20d. The outflow from the catalyst bed 20d is mixed with fresh ethylene from the line 14b in the bed front space 20b and enters the catalyst bed 20e. The process is repeated with the number of beds in the first alkylation reactor 20. Although three catalyst beds are displayed in the alkylation reactors 20, 30, more or less may be appropriate. The intermediate alkylation effluent from the first alkylation reactor 20 is transported to the second in line 8 :): the completion reactor 30. Before it is transported to the bed front space 30a, the heat exchanger 22 cools the effluent in line 18 to the desired firing temperature. Ethylene from the injection bed headspace 30a from line 14d is mixed with the intermediate alkylation effluent stream from line 18 and enters the catalyst bed 98299.doc -22-200533651 30d. The same process was repeated for the catalyst bed 30e & 30f, and the alkylation reactor effluent from the second alkylation reactor 30 was transported to the benzene 40 " Hollowerization reaction in line 32 The outflow can be depressurized by a pressure control valve not shown, and can be heated by a heater or heat exchanger, or both, which are not shown. Additionally ' more or less alkylation reactors may be suitable. If the alkylation reactors 20 and 30 and the transalkylation reactor 50 are operated in parallel as shown in Fig. I, benzene from the line 10 is routed to the transfaction reaction state 50 via the line 52. Line 54 carries polyethylbenzene (PEB) overhead diethylbenzene (DEB) and triethylbenzene (teb) from the top of PEB column 90, and is mixed with the bulk in line 52 to provide a transalkylation feed line 58. The transalkylation reactor 刈 includes three catalyst beds 50a-50c containing a transalkylation catalyst. More or less catalyst beds can be used in the transalkylation reactor 50. The transalkylation catalyst promotes the transalkylation reaction, in which ethyl groups from DEB and TEB are transalkylated with benzene to produce ethylbenzene. As a result, the official line 56 contains a greater concentration of ethylbenzene and a lower concentration of DEB and TEB than the transalkylation feed line 58. As shown in FIG. 1, the alkylation and transalkylation reactors are parallel, and three different materials are fed to the benzene column 40. The alkylation reactor effluent stream in line 32 and the trans-alkylation effluent stream in line 56 are fed with benzene, ethylbenzene, butylene RE and heavier PEBs into benzene column 40. Fresh feed benzene in line 12 is passed through a conventional adsorbent container stock containing a bed of clay or resin adsorbent 46 to adsorb impurities. The line contains 48 basic NCs from the benzene stream to purify the benzene to Stupid i go 40. The purified benzene stream typically contains between 400 and 800 milliseconds of " the sigma 40 is fed off into at least two streams. The top of the benzene column containing benzene *, the two leaves the benzene tower from the official line 62, and performs a condenser 64, in which the temperature is 98299.doc -23 · 200533651, but the temperature is between 120 ° C and 170 ° C. The condensing top enters the receiver 66, which includes traps for dispersing insoluble or free water in line 66a, and light gas in line 66b if necessary. The top hydrocarbon stream contaminated with ONCs including nitriles in line 68 is transported to the thermal adsorbent container 70, while a portion of the top hydrocarbon stream is returned to the benzene column 40. The top hydrocarbon stream includes 50 to 500 wppm water. The thermal sorbent container 70 contains a thermal sorbent molecular sieve bed 72 which is an acidic molecular sieve, which will adsorb ONCs including nitriles under appropriate conditions. The temperature and water concentration of the top hydrocarbon stream in line 68 are well adapted to selectively adsorb nitriles from the hydrocarbon stream with acid molecular sieves. Therefore, the denitrided benzene stream in line 10 does not actually contain ONCs, which is no more than 30 wppb. The bottom stream of the benzene column, which contains the product ethylbenzene and by-products including PEBs, leaves the column in line 74 and enters the ethylbenzene column 80. The ethylbenzene column 80 separates the benzene column bottoms stream from line 74 into two streams by distillation. The ethylbenzene column overhead stream containing the product ethylbenzene leaves the ethylbenzene column 80 in line 82 and is recovered from the process. The bottom stream of ethylbenzene tower contains by-products PEBs, generally including DEBs, TEBs and heavier PEBs, such as: butylbenzenes, dibutylbenzenes, tributylbenzenes, ethylbutylbenzenes, diethyl Butylbenzenes and diphenylethane. The ethylbenzene column bottoms leave the ethylbenzene column 80 in line 84 and pass through the PEB column 90. PEB column 90 separates the ethylbenzene column bottoms stream in line 84 into two streams. The underflow of the PEB tower containing PEBs heavier than TEB left in line 92 from the bottom of the PEB tower 90 and was rejected from the process. The top stream of the PEB column containing DEBs and TEBs exits from the PEB column 90 in line 54 and is recovered as previously described, mixed with the 98299.doc -24-200533651 feed in line 52 to the transalkylation reactor 50 . In the picture! The specific example in Figure 2 uses two sorbent beds that cooperatively remove ONCs from the calcined matrix feed when all of the textured matrix may be contaminated with ONCs. The resin or clay adsorbent ⑽ removes a large amount of ο ·, and at the same time, the thermal sorbent molecular sieve bed 72 adsorbs the remaining fluorene including nitriles, which poisons the tritiated and burnt catalyst. Figure 2 shows a method and apparatus which can be used with advantage when recovering benzene from another source such as: styrene monomer units. The method and apparatus are used to make total benzene for ethylbenzene. And recycled benzene from other sources may be contaminated with ONCs. All reference numerals of the components marked in Figure 2 correspond to the figure! Similar components in, but with different types are marked with a single point symbol (,). Otherwise, the same reference numerals are assigned to corresponding components having the same type in FIGS. I and 2. In addition, although ㈣2 shows that the calcination reactor and the transalkylation reactor are parallel, they can be operated in series. Fresh feed benzene in the official line 12 'flows through a conventional adsorbent container 44 containing a resin or clay adsorbent bed 4 6 to adsorb impurities including ◦ n cs from the benzene stream. Nitriles are expected in the fresh feed benzene in line 12 ,. The purified benzene stream typically contains 400 to 800 wppm water. Line 48, which carries the purified benzene stream ' combined with the benzene tower top stream in line 68, Phase I contains benzene, another source of gambling, and is carried in line 8 to the thermal adsorbent container. The benzene stream in line 8 is recovered from the styrene monomer unit and may contain water between 50 and 800 claws, and is generally water saturated. The thermal adsorbent container 70 contains an adsorption bed 72 of an acidic molecular sieve, which absorbs water under appropriate conditions and needs to be injected with ONCs including nitriles. If the water concentration is lower than 50 wppm 98299.doc -25- 200533651 into stupid stream. If the water concentration is higher than 50 Wppm, it is advantageous to dry the benzene stream. If the temperature of the benzene stream in line 8 is not at least 20 ° C, and preferably higher than us and not higher than 300 ° C, it must be heated or cooled to an appropriate temperature. This temperature range and water concentration are well suited for selective adsorption of nitriles from hydrocarbon streams, acidic molecular sieves, and basic NCs. Therefore, the denitrified benzene stream in line 32 does not actually contain 0 NCs to a detection amount of 30 wppb, is mixed with the purified benzene stream in line 48 ', and the top of the benzene column in line 68 The streams are mixed to provide a nitrogen-free benzene stream in line 10 ,. The benzene stream in the official line 10 'is sent to the alkylation reactors 20, 30 and is sent to the transalkylation reactor 50 through the parallel official line 52'. At line 10, the benzene in is transported to the alkylation reactors 20, 30 and reacts with the ethylene supplied from line 14 on a suitable catalyst, as explained with respect to Figure 丨. The alkylated effluent in line 32 is sent to a benzene column 40. The DEB and TEB from the overhead stream of PEB in line 54 are mixed with the benzene stream in line 52, to provide a transalkylation feed stream in line 58 which is sent to the transalkylation reactor 5 〇 中. The reaction of DEB and TEB with benzene in reactor 50 produces DEB and TEB with increased concentrations of ethylbenzene and the transalkylation effluent stream in line 56 relative to the transalkylation feed stream in line " Reduce the concentration. The transboiled effluent in line 56 is transported to the benzene column 40. The tower 40 separates the feed into at least two streams. The benzene-containing benzene column overhead stream leaves the benzene column via line 62, And enters the condenser 64, where it cools to a temperature between 120 ° C and 170 ° C. The condensation top enters the receiver 66, which is used to disperse the insoluble water in the line 66a, and if necessary The light gas trap in line 66b. In line 68, it contains most of the stupid 98299.doc -26- 200533651 top hydrocarbon stream, which was recovered to line 10 | A portion was refluxed to benzene column 4. The benzene tower bottom stream containing the product ethylbenzene and by-products including pEBs left the benzene tower in line 74 and entered the ethyl main column 80.

乙基苯塔80將苯塔塔底流分離成在管線82中之包含產物 乙基苯之乙基笨i合塔頂流、及在管線84中包含副產物 的乙基苯i合塔底流,其通過peb塔9〇。pEB塔將乙基苯 塔塔底流分離成在管線92中之、比ΤΕβ更重之pEBs的pEB 塔塔底流、及在管線54,中之PEB塔塔頂流,如前述被回收 到轉烷化反應器50中。 圖3顯示轉烷化反應器5〇及烷化反應器2〇、3〇,類似於 圖1操作。在圖3中標示元件的所有參考數字是相對應於圖 1中的颂似元件,但是具有不同型態會以雙逗點符號(,,)標 不。否則,相同參考數字被定為在圖i及3中、具有相同型 態的相對應元件。來自轉烷化反應器5〇之轉烷化反應器流 出流’可經由管線56”串聯到烷化反應器2〇,而非運送到 笨圪40。在管線32”中之;):完化反應器流出流、及在管線48 中之經純化苯流被按路徑送到苯塔4〇。在管線68中、來自 苯塔塔頂流的苯流,在熱吸附劑容器7〇中之熱吸附劑分子 篩床72上脫氮。在管線1〇中之脫氮笨流被轉向在管線52中 之轉浼化進料,並且在進入在管線58中之轉烷化反應器5〇 前,與在管線54中、來自PEB塔90的PEB塔塔頂流混合。 在管線56”中之轉烷化流出流與在管線1〇中之所餘脫氮苯 /瓜此&,並且進入烧化反應器、%,如關於圖工所敘述 98299.doc -27- 200533651 的。 圖4描述根據本發明用來生產異丙苯之裝置及製程的流 程。在管線100中之丙烯流與在管線102中之苯流混合,並 且管線1 01導入苯及丙稀的混合物到在烧化反應器12 〇中的 第一觸媒床122a。該烷化反應器120被顯示為向下流的反 應态’但疋向上流的反應器也為適當。觸媒床1 22a用於烧 化丙卸及本而產生異丙本的烧化觸媒。來自觸媒床122&之 流出流進入床間層空間124a。來自管線1〇6之回收烷化流 出k以熱父換器1 〇 8冷卻,並以分佈管線1 〇 6 a _ e及進料進 口管線104a-e回收到烷化反應器12〇中。從轉向管線1〇〇之 官線104中的丙烯,被分佈到進料進口管線l〇4a-e中,在 其中其分別與來自分佈管線106a_e的回收烷化流出流混 合。在進料進口管線1〇4a-e中之回收烷化流出流及丙烯混 合物被運送到各別的床間層空間124a-e,在其中其分別與 來自丽述觸媒床122a-e的流出流混合並個別進入後續觸媒 床122b-f。垸化流出流在管線1〇7中離開觸媒床122f。烷化 流出流的一部份藉著管線1〇6回收到烷化反應器12〇中,同 曰守另一部份在管線i 26被按路徑送到脫丙烷器塔丨3〇中。 在苢線110中之新鮮進料苯,在包含樹脂或黏土吸附劑 床114之習用吸附劑容器U2中被純化,移除鹼性的 ONCs。含4〇〇至8〇〇 wppm水之經純化苯流以管線ιΐ6被運 迗到脫丙烷器塔130中。脫丙烷器塔13〇中提供在管線132 中、包含苯和50至150 wPPm水的中間體流,並且溫度是至 夕I20 C,且較佳是大於125°C,並不超過170°C。這些性 98299.doc 200533651 質可被調整來製備在管線132中之苯流,來吸附腈類。在 一個具體實施例中,在管線132中之中間體流的溫度是來 自再沸器(未顯示)之脫丙烷器塔130中產生熱的結果,並且 該熱從脫丙烷器塔130、以在蒸餾塔中為一般設備的冷凝 器(未顯示)移除。若因此進料組合物或其他條件而水在苯 流中不足,水可被注入管線132中。另外,雖然在管線132 中之中間體流可為側面拉出,分隔壁塔可用來提供較佳的 中間體切出物(cut)。脫丙烷器塔130拒絕在管線134中、塔 頂流之丙烷及過量的水。比丙烷更重的烴經由管線US 中、土合底流移出,並且運送到苯塔140。 在其與在管線152中之轉烷化流出流混合之後,苯塔14〇 接收在官線136中、來自脫丙烷器塔13〇底部的進料。苯塔 140產生在管線142中之包含苯的苯塔塔頂流、及在管線 144中之包含乙基苯及pEBs的苯塔塔底流。在管線Μ〕中之 苯塔塔頂流可以水濃度5〇至15〇 wppm,並且温度是至少 120°C,且較佳是大於125t,並不超過17〇它。在管線η〕 中之脫丙烷器中間體流具有類似的性質,並且與流丨42組 合,並且以管線161運送到熱吸附劑容器16〇。熱吸附劑容 為1 60包含酸性分子篩吸附床,用來移除,包括在管 線161中、來自混合苯流的腈類。在管線164中之脫氮苯流 出流藉著管線1〇2被運送到烷化反應器12〇、及藉著管線 166被運送到轉燒化反應器15〇。在管線166中之苯流:來 自重物塔190、在官線168中之含二異丙基苯(dib)的中間 體流混合。在管線154中之苯及mB的混合物被運送到轉烷 98299.doc -29- 200533651 化反應為150中。DIB與苯在在轉烷化反應器15〇中之轉烷 化觸媒床156上轉烧化,產生異丙苯。在管線152中之轉燒 化級出飢,比官線丨54中具有較大濃度的異丙苯及較小 度的苯和DIB。 在&線144中之苯塔塔頂流被運送到異丙苯塔丨8〇中。異 丙本塔180提供含產物異丙苯的異丙苯塔頂流,其被回收 到管線182中。在管線184中之異丙苯塔塔頂流包含比異丙 苯更重的烴類,被運送到重物塔190。重物塔1 90產生在管 線1 68中之含DIB的中間體流。在重物塔頂流中的較輕物質 在官線192中被移除,並且重物塔底流在管線194中被移 除。 圖5顯示類似於圖4的流程,除了新鮮苯流在包含樹脂或 4占土及附劑床114之習用吸附劑容器112中被純化,並且然 後在進入脫丙烷器塔13〇之前,在熱吸附劑容器16〇中被脫 氮。在圖5中標示元件的所有參考數字是相對應於圖4中的 犬員似元件’但是具有不同型態會以單逗點符號(,)標示。否 則,相同參考數字被定為在圖4及5中、具有相同型態的相 對應元件。管線丨1〇,傳遞新鮮進料苯到習用吸附劑容器U2 中’管線116’運送來自吸附劑容器U2之經純化苯到包含酸 性分子篩吸附床1 62的熱吸附劑容器丨60,並且管線丨64,進 料脫氮的苯到脫丙烷器塔丨3〇。來自脫丙烷器塔丨3〇、在管 線132’中之中間體流,在管線1〇2,中與來自苯塔塔頂流、 在苯塔140之管線142中的苯混合並送至烷基化反應器 1 20 °否則,圖5中的流程大致如圖4地操作。 98299.doc -30- 200533651 圖6顯示類似於圖5的流程,但是熱吸附劑床i62,,被提供 於轉炫化反應器。在圖6中標示元件的所有參考數 字是相對應於圖4中的類似元件,但是具有不同型態會以 雙逗點符號r)標示。否則,相同參考數字被定為在圖4及6 中、具有相同型態的相對應元件。在管線11〇的苯在包含 樹脂或黏土吸附劑床114之習用吸附劑容器112中被純化鹼 性〇NCs。管線116進料經純化苯,與來自烷化反應器 120、在官線126中之烷化流出流流到脫丙烷器塔13Q。在 笞線1 3 2中之脫丙烧裔中間體流被運送,並且與來自苯拔 塔頂流、經由管線166”轉向管線142中的苯混合,並且被 進料到轉烷化反應器150”。控制閥188調節來自重物塔 190、在管線168中之重物中間體流裡的多少dib,與在管 線1 66中轉向本塔頂流混合,並且多少繞過管線154,,、經 過繞道管線186。轉烷化反應器15〇”包括酸性分子篩觸媒 之犧牲性熱吸附劑床162”,用來吸附包括腈類的〇NCs。 來自犧牲性熱吸附劑床162”的脫氮進料在床間層空間157 中’與來自繞道管線186的DIB混合,並且進入轉烷化觸媒 床156”。DIB與苯在轉烷化觸媒床156”上轉烷化,產生異 丙本在^線1 5 2中之轉烧化流出流’比在管線1 $ 4中具有 較大濃度的異丙苯及較低濃度的苯及DIB。在管線丨52中之 轉烧化流出流與在管線丨36中之脫丙烷器塔底流混合,並 且進料到苯塔140中。 在管線110中之新鮮苯流中、不被習用吸附劑容器11 2所 吸附、並且不在管線134中、脫丙烷器塔頂流中被拒絕的 98299.doc 31 200533651 所有腈類,會存在於管線132”中之中間體流裡。無腈類會 存在於管線136中之脫丙烷器塔底流裡。在管線11〇中、來 自新鮮進料笨流、在製程中存活的所有腈類,會在管線 =2,’中。管線166”中之流只向箭號"A”的方向。因此,在 管線132”中的所有腈類會被導向犧牲性熱吸附劑床162,,, 以移除腈類。無腈類由管線166,,中旅行到管線ι〇2"中。因 為無腈類會在管線168中之中間體流裡,較佳地所有的重 中門體机會經由繞道官線丨86繞過犧牲性熱吸附劑床 162,、 在圖7中的流程不同於在圖6中的流程,其中於管線 2中之脫丙烷|§中間體流結合來自管線142中的苯塔塔 頂流’形成於管線1G2,,,中之苯進料流,並且犧牲性熱吸附 劑床162”是燒化反應器12『的引導床。在圖7中標示元件 的所有參考數字是相對應於圖4中的類似元件,但是具有 不同型恶會以二逗點符號標示。否則’相同參考數字 被定為在圖4及7中 '具有相同型態的相對應元件。於管線 102’’’中之苯進料流只流向箭號”β"的方向。如圖6中的流 程’在管線11〇中' 來自新鮮進料苯流、在製程中存活的 :有腈類,會在管線132…中。管線132…中的所有腈類會 導向在燒化反應器120…中之犧牲性熱吸附劑床162,,,, 以移除腊類。 來自犧牲性熱吸㈣床162,,,之脫氮苯流出流進入床間 層空間124a’’’,在盆中豆血丨、,从 在,、中/、,、U管線l〇4a,,,分佈的丙烯混 5 。來自管、線1〇6…之冷卻燒化流出流藉著分佈管線 98299.doc -32· 200533651The ethylbenzene column 80 separates the bottom stream of the benzene column into an ethylbenzene i-th column top stream containing product ethylbenzene in line 82 and an ethylbenzene i-th column bottom stream containing by-products in line 84, which Via Peb Tower 90. The pEB column separates the ethylbenzene column bottom stream into pEB column bottom stream in line 92, which is pEBs heavier than TEβ, and PEB column overhead stream in line 54, which are recovered as described above for transalkylation. Reactor 50. Fig. 3 shows the transalkylation reactor 50 and the alkylation reactors 20 and 30, which are operated similarly to Fig. 1. All the reference numerals of the components marked in FIG. 3 correspond to the ode-like components in FIG. 1, but the different types are marked with a double comma (,,). Otherwise, the same reference numerals are assigned to corresponding components having the same type in Figs. I and 3. The transalkylation reactor effluent stream from the transalkylation reactor 50 may be connected in series to the alkylation reactor 20 via line 56 "instead of being transported to the reactor 40. In line 32";): Finishing The reactor effluent stream and the purified benzene stream in line 48 were routed to a benzene column 40. The benzene stream from the top stream of the benzene tower in line 68 is denitrified on the thermal adsorbent molecular sieve bed 72 in the thermal adsorbent container 70. The denitrification stream in line 10 is diverted to the transalkylation feed in line 52, and before entering the transalkylation reactor 50 in line 58, and from line 54 from the PEB column 90 PEB tower tower top stream mixed. The transalkylation effluent in line 56 "and the remaining deazabenzene / melon in line 10 & and enter the calcination reactor, as described in the drawing 98299.doc -27- 200533651 Figure 4 depicts the process and equipment used to produce cumene according to the present invention. The propylene stream in line 100 is mixed with the benzene stream in line 102, and line 101 introduces the benzene and propylene mixture to The first catalyst bed 122a in the calcination reactor 120. The alkylation reactor 120 is shown as a downflow reaction state, but a sloping upflow reactor is also appropriate. The catalyst bed 1 22a is used to burn propylene The sintering catalyst that is isopropyl is discharged, and the effluent from the catalyst bed 122 & enters the bed space 124a. The recovered alkylation effluent k from the line 106 is cooled by the hot parent converter 108. And the distribution line 106a_e and the feed inlet lines 104a-e are recovered into the alkylation reactor 120. The propylene in the official line 104 from the diverting line 100 is distributed to the feed inlet line 1. 〇4a-e, where they are respectively mixed with recovered alkylation effluent streams from distribution lines 106a-e The recovered alkylated effluent stream and propylene mixture in the feed inlet lines 104a-e are transported to the respective interbed spaces 124a-e, where they are separately associated with those from the Lishu catalyst beds 122a-e. The effluent streams are mixed and individually enter the subsequent catalyst beds 122b-f. The tritiated effluent stream leaves the catalyst bed 122f in line 107. A portion of the alkylated effluent stream is recovered to the alkylation reactor via line 106. At 12 o’clock, the other part of the same line was routed to the depropanizer tower 30 in line i 26. The fresh feed benzene in the squall line 110 was placed in the resin or clay adsorbent bed 114. The conventional adsorbent container U2 is purified to remove alkaline ONCs. A purified benzene stream containing 400 to 800 wppm water is transported to the depropane tower 130 via the line ιΐ6. The depropane tower 13 〇 An intermediate stream containing benzene and 50 to 150 wPPm water in line 132 is provided, and the temperature is up to I20 C, and preferably greater than 125 ° C and not more than 170 ° C. These properties are 99299.doc 200533651 can be adjusted to prepare a benzene stream in line 132 to adsorb nitriles. In a specific embodiment, in line 132 The temperature of the intermediate stream is a result of the heat generated in the depropane column 130 from the reboiler (not shown), and the heat from the depropane column 130 to a condenser (not shown) which is a general device in the distillation column (Shown) removed. If water is insufficient in the benzene stream due to feed composition or other conditions, water can be injected into line 132. In addition, although the intermediate stream in line 132 can be pulled out sideways, the dividing wall column It can be used to provide a better intermediate cut. Depropanizer column 130 rejects propane and excess water in line 134 at the top of the column. Heavier hydrocarbons than propane are removed via line US, earthen bottom stream, and transported to benzene column 140. After it is mixed with the transalkylated effluent stream in line 152, the benzene column 14o receives the feed in the official line 136 from the bottom of the depropanizer column 13o. The benzene column 140 generates a benzene column top stream containing benzene in line 142 and a benzene column bottom stream containing ethylbenzene and pEBs in line 144. The top stream of the benzene tower in line M] may have a water concentration of 50 to 15 wppm and a temperature of at least 120 ° C, and preferably more than 125 t, and not more than 170. The depropanizer intermediate stream in line n] has similar properties and is combined with stream 42 and is conveyed to the thermal adsorbent container 16 by line 161. The thermal sorbent capacity of 1 60 contains an acidic molecular sieve adsorption bed for removal, including nitriles in line 161 from the mixed benzene stream. The denitrified benzene outflow in line 164 is conveyed to the alkylation reactor 120 through the line 102 and to the trans-boiler reactor 15 through the line 166. Benzene stream in line 166: Intermediate stream from distillate column 190 and diisopropylbenzene (dib) in official line 168 are mixed. The mixture of benzene and mB in line 154 is transported to the transalkylation 98299.doc -29- 200533651 to a reaction of 150. DIB and benzene are fired on a transalkylation catalyst bed 156 in a transalkylation reactor 15 to produce cumene. The reburning stage in line 152 is hungry, which has a higher concentration of cumene and a lower degree of benzene and DIB than in official line 54. The top stream of the benzene tower in & line 144 is transported to the cumene tower 80. The isopropylbenzene column 180 provides an cumene overhead stream containing the product cumene, which is recovered into line 182. The top stream of the cumene column in line 184 contains heavier hydrocarbons than cumene and is transported to a weight column 190. The weight column 190 produces a DIB-containing intermediate stream in line 168. The lighter material in the top stream of the heavy tower is removed in line 192, and the bottom stream of the heavy tower is removed in line 194. FIG. 5 shows a flow similar to that of FIG. 4 except that the fresh benzene stream is purified in a conventional adsorbent container 112 containing a resin or 4 occupant and a bed 114, and then before entering the depropanizer column 130, in the heat The adsorbent container 160 is denitrified. All the reference numerals of the components marked in FIG. 5 correspond to the canine-like components' in FIG. 4 but have different types and are indicated by a single comma (,). Otherwise, the same reference numerals are assigned to corresponding components having the same type in FIGS. 4 and 5. Line 10, passing fresh feed benzene to the conventional adsorbent container U2, 'line 116', transports purified benzene from the adsorbent container U2 to a thermal adsorbent container 60 containing an acidic molecular sieve adsorption bed 1 62, and the line 64. Feed denitrogenated benzene to a depropanizer column 30. The intermediate stream from the depropanizer column 30, in line 132 ′, is mixed with the benzene from the top stream of benzene column, in line 142 of benzene column 140, and sent to the alkyl group in line 102. Chemical reactor 1 20 ° Otherwise, the flow in FIG. 5 operates roughly as in FIG. 4. 98299.doc -30- 200533651 Fig. 6 shows a flow similar to that of Fig. 5, except that the thermal adsorbent bed i62, is provided to the conversion reactor. All reference numerals of the components marked in Fig. 6 correspond to similar components in Fig. 4, but with different types, they are indicated by double comma r). Otherwise, the same reference numerals are assigned to corresponding elements having the same type in FIGS. 4 and 6. Benzene in line 110 is purified with basic NCs in a conventional adsorbent container 112 containing a resin or clay adsorbent bed 114. Line 116 is fed with purified benzene and the alkylation effluent from alkylation reactor 120 in line 126 flows to depropanizer column 13Q. The deprotonated intermediate stream in the squall line 1 3 2 is transported and mixed with benzene from the overhead stream of the benzata, diverted via line 166 "to line 142, and fed to the transalkylation reactor 150. ". The control valve 188 regulates how much dib from the heavy column 190, the heavy intermediate flow in line 168, is mixed with diverting to the top stream of this column in line 1 66, and bypasses line 154 to a certain extent, 186. The transalkylation reactor 15 ″ includes a sacrificial thermal adsorbent bed 162 ″ of an acidic molecular sieve catalyst for adsorbing ONCs including nitriles. The denitrified feed from the sacrificial thermal adsorbent bed 162 "is mixed in the interbed space 157 'with the DIB from the bypass line 186 and enters the dealkylation catalyst bed 156". DIB and benzene are transalkylated on the transalkylation catalyst bed 156 ", resulting in the trans-baking effluent stream of isopropyl in line 152, which has a higher concentration than cumene in line 1 $ 4 and Lower concentrations of benzene and DIB. The transboiler effluent stream in line 52 is mixed with the depropanizer bottoms stream in line 36 and fed to the benzene column 140. In the fresh benzene stream in line 110 98299.doc 31 200533651 which is not adsorbed by the conventional adsorbent container 11 2 and is not rejected in the overhead stream of the depropane column in line 134. All nitriles will be present in the intermediate stream in line 132 ". Nitriles-free species will be present in the depropanizer bottoms stream in line 136. In line 110, all nitriles from the fresh feed stupid stream that survive the process will be in line = 2, '. The flow in line 166 "only goes in the direction of the arrow" A ". Therefore, all nitriles in line 132 "will be directed to the sacrificial thermal sorbent bed 162 ,, to remove nitriles. Nitrile-free travels from line 166, to line ι02 " because there is no The nitriles will be in the intermediate flow in line 168. Preferably, all the heavy doors will bypass the sacrificial thermal adsorbent bed 162 via the bypass line 86. The flow in FIG. 7 is different from that in The flow in Figure 6 where the depropane in line 2 | § Intermediate stream combined with the benzene column overhead stream from line 142 is formed in line 1G2, benzene feed stream, and sacrificial thermal adsorption The agent bed 162 "is a guide bed for the calcination reactor 12". All the reference numerals of the components marked in Fig. 7 correspond to similar components in Fig. 4, but with different types of evils, they are marked with two commas. Otherwise, the same reference numerals are designated as corresponding elements having the same type in FIGS. 4 and 7. The benzene feed stream in line 102 '' 'only flows in the direction of the arrow "β". As shown in the process of Figure 6' in line 11 ', the benzene stream is from a fresh feed benzene stream and is alive in the process: with nitrile Will be in line 132 .... All nitriles in line 132 ... will be directed to the sacrificial thermal adsorbent bed 162 ,, in the calcination reactor 120 ... to remove wax. From sacrificial heat absorption The denitrified benzene effluent from the bed 162 ,, and enters the bed interlayer space 124a '' ', the soybean blood in the basin, and the propylene distributed from the U, 104, and U pipelines. Mixing 5. Cooling and calcination effluent from pipe, line 106, ... through distribution line 98299.doc -32 · 200533651

1〇6π-6·’|被回收到烧化反應器12〇,,,,到進料進口管線 1 04b -e 。於官線1 〇4中之丙烯被分佈到進料進口管線 104b-e,在其中其分別與來自分佈管線丨〇6b",_e|"之回收烷 化流出流混合。在進料進口管線1〇4b,,,_en,中的回收烷化 流出流及丙烯的混合物,被運送到各別的床間層=間 124b -e ,在其中其分別與來自前述觸媒床122b,,,_e,,,的 流出流混合,並且分別進入後續的觸媒床122c",_f,"。烷化 流出流於管線107中離開最後觸媒床122fn。一部份的烷化 流出流藉著管線106”,被回收到烷化反應器12〇,,,,同時另 一部份在管線126被按路徑送到脫丙烷器塔13〇中。1〇6π-6 · ′ | was recovered to the calcination reactor 120, and, to the feed inlet line 104b-e. The propylene in the official line 104 is distributed to the feed inlet lines 104b-e, where they are respectively mixed with the recovered alkylation effluent stream from the distribution line 〇06b ", _e | ". The recovered alkylated effluent stream and the propylene mixture in the feed inlet line 104b ,, _en, are transported to the respective bed layer = bay 124b-e, where they are separately associated with the catalyst bed from the aforementioned catalyst bed. 122b ,,, _ e ,,, and the outflows are mixed and enter the subsequent catalyst beds 122c ", _ f, " respectively. The alkylation effluent leaves the last catalyst bed 122fn in line 107. A part of the alkylation effluent is recovered to the alkylation reactor 120 through the line 106 ", while another part is routed to the depropanizer column 13 through the line 126.

圖8描述組合圖6及7中類似元件的流程,是使用兩個犧 牲性熱吸附劑床。在圖8中標示元件的所有參考數字是相 對應於圖4中的類似元件,但是具有不同型態會以十字符 號(t)標示。否則,相同參考數字被定為在圖4及8中、具有 相同型態的相對應元件。—個犧牲性熱吸賴床_提供 於轉烷化反應器15〇t中,如關於圖6所述,並且第二個犧 牲性熱吸附劑床16沘提供於烷化反應器12吋中,如關於圖 7所述。管線132卞中之脫丙烷器塔中間體流被分成兩個物 /J,L S線1 33中運送之轉烷化苯進料流,與管線142中、經 由官線166t轉向的來自苯塔塔頂流混合,並且經由管線 1 54t進料到㈣化反應15〇。酸性分子篩觸媒的犧牲性熱 吸附劑床162a,吸附來自進料流、包括腈類的〇NCs。來 自犧牲性熱吸附劑床162a的脫氮進料,與來自繞道管線 186的DIB在床間層空間157混合,並且進入轉烷化觸媒床 98299.doc -33- 200533651 1 56f。DIB與苯在轉烧化觸媒床1 56*f上轉燒化,產生異丙 笨。管線1 52中之轉烧化流出流,比管線1 54卞中具有較大 濃度的異丙苯及較小濃度的苯和DIB。管線1 52中之轉院化 流出流與管線136中之脫丙烷器塔底流混合,並且進料到 苯塔140。 衍生自管線132t中之脫丙烷器塔中間體流的管線135中 第二流,結合來自管線142的苯塔塔頂流,形成管線1〇討 中的苯進料流,並且被運送到第二犧牲性熱吸附劑床 祕’導向烧化反應器12〇卜來自犧牲性熱吸附劑床祕 的脫氮苯流出流,進入床間層空間124a,在其中與由管線 l〇4t分佈的丙烯混合。在烷化反應器叫之烷化如關於圖 7中所解釋的進行。來自烧化反應器的流出流,在管 線126中被運送到脫㈣器塔UG。因為在管線i6q中之經 轉向苯流只流向箭號” A”的方向,並且在管線1〇討中之苯 進=流只流向箭號"B"的方向。在管線11〇中、來自新鮮進 料本,、在製程中存活的所有腈類,會在管線MM中。因 匕s線1 32卞中的所有腈類會被導向在轉烧化反應器中之 犧牲性熱吸附劑床162a、或烧化反應器12〇卞中之犧牲性熱 及附劑床162b,以移除所有所餘的GNCs,包括低至30 wPPb的腈類。 圖9描述根據本發明用來生產異丙苯之另外流程,不使 用脫丙烧器塔。在圖9中標示元件的所有參考數字是相對 應於圖4中的類似元件,但是具有不同型態會以雙十字符 波⑴標示。否則’相同參考數字被定為在圖4及9中、具有 98299.doc -34- 200533651 相同型態的相對應元件。在管線丨丨吋中、包含4〇〇至8〇〇 wppm水的新鮮進料苯,在包含樹脂或黏土吸附劑床1 μ之 習用吸附劑容器i丨2中被純化,移除鹼性的〇NCs。在管線 116$中之經純化苯視情況地在熱交換器丨丨7中加熱,並且 以管線161 ί運送到熱吸附劑容器16〇中。熱吸附劑容器16〇 包含酸性分子篩吸附劑床162,用來移除〇NCs,包含在管 線161中、來自經純化苯流的腈類。在管線“竹中之脫氮 笨々丨L出級與在管線136ί中之經組合烧化及轉烧化流出流 混合,並且運送到苯塔14〇。 苯塔140產生包含在管線142丨中之苯的苯塔塔頂流,及 在官線144中之包含乙基苯及PEBs的苯塔塔底流。在管線 142ί中之塔頂苯流可被提供為有水濃度高至5〇〇 wppm,並 且溫度疋至少120°C,且較佳是大於125。〇,並不超過170°C。 在官線142J中之塔頂苯流的一部份藉著管線166$被轉向轉 烷化反應器150。在重物塔中間體流中、藉著管線168運送 的DIB,與在管線166ί的苯混合,提供在管線154丨中之轉 烷化進料流。DIB在轉烷化反應器15〇中之轉烷化觸媒床 156上、以苯轉烷化,產生異丙苯。在管線152中之轉烷化 流出流,比管線1 54J中的具有較大濃度的異丙苯及較小濃 度的苯和DIB。在管線102J中之所餘的苯塔塔頂流,在烷 化反應器120中之烷化觸媒床上與丙烯反應,如關於圖4所 敘述的。在管線1 26 J中之烧化流出流,與在管線ί 52中之 轉烷化流出流混合,在管線136;^中提供經組合的流出流。 在管線144中之苯塔塔底流被運送到異丙苯塔丨8〇。異丙 98299.doc -35- 200533651 苯塔1 8 0提供包含產物異丙苯的異丙苯塔頂流,其在管線 182中被回收。在管線184中之異丙苯塔底流包含比異丙苯 更重的烴類,被運送到重物塔190。重物塔19〇產生在管線 1 68中、包含DIB的中間體流。在重物塔頂流中的較輕物質 在管線192中被移除,並且重物塔底流在管線194中被移 除。 必須注意:在一些圖示中,如接收器、再沸器、冷凝器 及/或回流管線的設備,對一些設備為詳細的,但在其他 並不。然而,在敘述及圖示中的此細節省略不指示此設備 不被考里’但習知此藝者會知道何種設備為必需的。 本發明進一步以考量下列實例而清楚,其意欲純為示範 本發明之用途。 實例Figure 8 depicts the flow of combining similar elements in Figures 6 and 7, using two sacrificial thermal adsorbent beds. All reference numerals of the components marked in FIG. 8 correspond to similar components in FIG. 4, but they have different types and are indicated by a ten character (t). Otherwise, the same reference numerals are assigned to corresponding elements having the same pattern in Figs. A sacrificial heat absorption bed_ provided in the transalkylation reactor 150t, as described with respect to FIG. 6, and a second sacrificial heat sorbent bed 16 沘 is provided in the alkylation reactor 12 inches, As described with respect to FIG. 7. The depropanizer column intermediate stream in line 132 卞 is divided into two streams / J, the transalkylated benzene feed stream carried in LS line 1 33, and the top stream from the benzene tower diverted via line 166t in line 142. Mix and feed to the tritiation reaction 150 via line 54t. The sacrificial thermal sorbent bed 162a of the acidic molecular sieve catalyst adsorbs NCs from the feed stream, including nitriles. The denitrified feed from the sacrificial thermal adsorbent bed 162a is mixed with the DIB from the bypass line 186 in the interbed space 157 and enters the transalkylation catalyst bed 98299.doc -33- 200533651 1 56f. DIB and benzene were trans-fired on a trans-fired catalyst bed 156 * f, which produced isopropylbenzene. The transboiled effluent in line 1 52 has a greater concentration of cumene and a lower concentration of benzene and DIB than in line 1 54 卞. The diverted outflow in line 152 is mixed with the depropanizer column bottom line in line 136 and fed to benzene column 140. The second stream in line 135, which is derived from the depropanizer column intermediate stream in line 132t, combines the benzene column overhead stream from line 142 to form the benzene feed stream in line 10 and is transported to the second The sacrificial thermal adsorbent bed is directed to the sintering reactor 1220. The denitrogenated benzene effluent from the sacrificial thermal adsorbent bed is entered into the bed interlayer space 124a, where it is mixed with propylene distributed by the line 104t. The alkylation in the alkylation reactor is performed as explained with respect to FIG. The effluent stream from the calcination reactor is carried in line 126 to the stripper column UG. Because in the pipeline i6q, the benzene flow turns only in the direction of the arrow "A", and in the pipeline 10, the benzene flow = the flow only flows in the direction of the arrow " B ". In line 110, all the nitriles from the fresh feedstock that survive the process will be in line MM. Because all of the nitriles in line 1 32 卞 will be directed to the sacrificial thermal adsorbent bed 162a in the trans-sintering reactor or the sacrificial heat and additive bed 162b in the calcining reactor 120 ° to remove all The remaining GNCs include nitriles as low as 30 wPPb. Fig. 9 depicts another process for producing cumene according to the present invention without using a depropanizer column. All the reference numerals of the components marked in FIG. 9 correspond to similar components in FIG. 4, but with different types, they are indicated by double ten characters. Otherwise, the same reference numerals are assigned to corresponding elements having the same type as 98299.doc -34- 200533651 in Figs. 4 and 9. Fresh feed benzene containing 400 to 800 wppm water in the line is purified in a conventional adsorbent container i 2 containing 1 μ of resin or clay adsorbent bed, removing the alkaline 〇NCs. The purified benzene in line 116 $ is optionally heated in a heat exchanger 丨 7 and transported to the thermal adsorbent container 160 in line 161. The thermal sorbent container 16o contains an acidic molecular sieve sorbent bed 162 for removing the NCs, and the nitriles contained in the line 161 from the purified benzene stream. The denitrification stage L in the bamboo line is combined with the combined sintering and trans-sintering effluent stream in the line 136 and is transported to the benzene column 140. The benzene column 140 produces the benzene contained in the line 142 丨The top stream of the benzene tower, and the bottom stream of the benzene tower containing ethylbenzene and PEBs in the official line 144. The top benzene stream in the line 142, can be provided with water concentration as high as 500 wppm, and the temperature疋 At least 120 ° C, and preferably greater than 125 °, and not more than 170 ° C. A portion of the overhead benzene stream in the official line 142J is diverted to the dealkylation reactor 150 via line 166 $. The DIB carried in the heavy column intermediate stream via line 168 is mixed with benzene at line 166 and provides a transalkylation feed stream in line 154. The DIB is in the transalkylation reactor 15 The transalkylation catalyst bed 156 is transalkylated with benzene to produce cumene. The transalkylation effluent in line 152 has a greater concentration of cumene and a lower concentration than those in line 1 54J. Benzene and DIB. The remainder of the benzene column overhead in line 102J is reacted with propylene on the alkylation catalyst bed in the alkylation reactor 120. As described in relation to Figure 4. The calcined effluent in line 1 26 J is mixed with the transalkylated effluent in line 52 to provide a combined effluent in line 136; ^ at line 144 The bottom stream of the benzene tower is transported to the cumene tower. 80. The isopropyl 98299.doc -35- 200533651 benzene tower 1 80 provides the cumene tower overhead stream containing the product cumene in line 182. Recovered. The cumene column bottom stream in line 184 contains heavier hydrocarbons than cumene and is transported to weight column 190. Weight column 190 produces an intermediate stream containing DIB in line 1 68 The lighter material in the top stream of the heavy column is removed in line 192, and the bottom stream of the heavy column is removed in line 194. It must be noted that in some illustrations, such as the receiver, reboiler, The equipment of the condenser and / or return line is detailed for some equipment, but not for others. However, the omission of this detail in the description and illustration does not indicate that the equipment is not tested. It will be known what kind of equipment is necessary. The present invention is further made clear by considering the following examples, which are intended to be pure Exemplary use of the present invention. Examples

實例I 測試進行以測定酸性分子篩在低溫下、從含水之苯流中 吸附乙腈的有效性。吸附劑以擠壓約8〇重量沸石及2〇 重里%氧化鋁黏合劑而製備。在乾燥之後,吸附劑被壓碎 並且在20至40篩之間的顆粒被負載到八個串聯流體流通的 容器中。苯進料以500 wppn^〇水飽和,並且wppm乙 腈負載,在室溫及室壓下流經串聯的八個吸附劑容器。 以經吸附氮相對於平均在八個吸附劑床之吸附劑而言, 最終負載為0.125重量%。在前五個床上的吸附劑具有其吸 附容量,料乙腈在-天内通過該床,並^在六到八床中 的吸附劑在兩天内吸附其容量。 98299.doc -36- 200533651 然後,來自該床的吸附劑在5〇°c下、以水洗滌—小時。 九十七百分比的氮從吸附劑被萃取。因此,在較低溫度 下,水損害乙腈的吸附、及/或較優於乙腈被吸附。Example I A test was performed to determine the effectiveness of acidic molecular sieves to adsorb acetonitrile from an aqueous benzene stream at low temperatures. The adsorbent was prepared by extruding about 80 weight percent zeolite and 20 weight percent alumina binder. After drying, the sorbent is crushed and the particles between 20 and 40 sieve are loaded into eight vessels in series fluid circulation. The benzene feed was saturated with 500 wppn ^ water and wppm acetonitrile supported, and passed through eight adsorbent vessels in series at room temperature and room pressure. The final loading was 0.125% by weight of adsorbed nitrogen relative to the adsorbent averaged over eight adsorbent beds. The adsorbent in the first five beds has its adsorption capacity, and acetonitrile passes through the bed in one day, and the adsorbent in the six to eight beds adsorbs its capacity in two days. 98299.doc -36- 200533651 Then, the adsorbent from the bed was washed with water at 50 ° C for one hour. Ninety-seven percent of the nitrogen is extracted from the sorbent. Therefore, at lower temperatures, water impairs the adsorption of acetonitrile and / or is better than acetonitrile being adsorbed.

實例II 一系列的測試被進行,以比較黏土、樹脂及分子筛吸附 劑對乙腈的吸附表現。該吸附劑被負載到八個串聯流體流 通的容器中。苯進料以500 wppm的水飽和,並且各以 1 wppm乙腈、NFM及NMP負載的目標物,在室溫及室声 下流經串聯的八個吸附劑容器。一個實驗的笨進料沒有 水。Y沸石以擠壓約80重量%丫_沸石及2〇重量%氧化銘黏合 劑而製備。 表I比較有機氮不純物通過所選吸附劑床所花的時間。Example II A series of tests were performed to compare the adsorption performance of clay, resin, and molecular sieve adsorbents for acetonitrile. The sorbent was loaded into eight vessels in series with fluid flow. The benzene feed was saturated with 500 wppm water, and each of the targets loaded with 1 wppm acetonitrile, NFM, and NMP flowed through eight sorbent vessels in series at room temperature and room sound. An experimental stupid feed had no water. Y zeolite is prepared by extruding about 80% by weight of Y-zeolite and 20% by weight of oxide binder. Table I compares the time it takes for organic nitrogen impurities to pass through the selected adsorbent bed.

表I 吸附劑 黏土 (SC-626GS) 樹脂 (A-15) Y彿石 Y沸石 料 ~ 水飽和 水飽和 水飽和 萆乞燥 ACN通過起初床(天) 立刻 0.9 立刻 0.1 ACN通過第八床(天) 1.6 0.8 _0.1 5.0 NMP通過起初床(天) 6.9 立刻 1_0.1 0.1 NMP通過第八床(天) 30.6 >15 >7 >8 NFM通過起初床(天) 6.9 立刻1 ~~〇7\~~ 0.1 NFM通過第八床(天) i吸附劑上的氮 >30 〇 15.0 —"L4~~ _6.7 ~09~~~ 7.0 ~~08~ 表I私出在這些條件下,無一床有效地吸附乙腈一段長時 間若使用夠大床,Υ沸石可有效地從乾燥進料中適當吸 人m 別丄μ | 13 1.4 附乙腈’ I因為通過起減為早,但是在第八床合理地延 長。黏土吸附劑似乎是對ΝΜρ及nfm最以。樹脂似乎只 98299.doc 200533651 、夠大床的樹脂吸附劑時,適當地吸附NMP及NFM, 因為通過起初床為立刻,但是在第八床延長了。Table I Adsorbent Clay (SC-626GS) Resin (A-15) Y Fossil Y Zeolite ~ Water Saturated Water Saturated Water Saturated 萆 ACN through the initial bed (days) immediately 0.9 immediately 0.1 ACN through the eighth bed (days) ) 1.6 0.8 _0.1 5.0 NMP passes the initial bed (days) 6.9 immediately 1_0.1 0.1 NMP passes the eighth bed (days) 30.6 > 15 > 7 > 8 NFM passes the initial bed (days) 6.9 Immediate 1 ~~ 〇7 \ ~~ 0.1 NFM passes through the eighth bed (day) i Nitrogen on the adsorbent > 30 〇15.0 — " L4 ~~ _6.7 ~ 09 ~~~ 7.0 ~~ 08 ~ Under the conditions, no bed can effectively adsorb acetonitrile for a long period of time. If a large bed is used, the zeolite can effectively absorb the appropriate amount from the dry feed. M Don't make μ | 13 1.4 Acetonitrile 'I is passed early because But the eighth bed is reasonably extended. Clay sorbents appear to be the best for NMρ and nfm. Resin appears to be only 98299.doc 200533651, which is a large bed of resin adsorbent, which properly adsorbs NMP and NFM, because passing through the initial bed is immediate, but extended in the eighth bed.

實例III ^ #系歹】的’則5式被進行,以評估從苯移除乙腈(ACN),是 藉與擦壓約8〇重量%γ。、弗石及別重量%氧化铭黏合劑 $衣備的吸附劑接觸。吸附劑具有ABD 0.625克/立方公 :對所有的測試,吸附劑在負載25克吸附劑到容器之 月』於120 C下乾燥2小時。測試在24°C及150°C的操作溫 度下進行,並且變化進料苯中的水份量。 用於測试的進料是以ACN攙入苯流中製備,以產生約2〇 WPPm虱的目標物。在其與ACN攙合之前,起始苯進料被 乾秌。在測試中的兩個,苯進料與水攙合,以測定水對氮 四個測滅之失效吸附劑分析的結果摘要於表 II中。 、Formula III of Example III ^ # 系 歹] was performed to evaluate the removal of acetonitrile (ACN) from benzene by rubbing with about 80% by weight of γ. , Fu Shi and other weight% oxide Ming adhesive $ clothing preparation adsorbent contact. The sorbent has an ABD of 0.625 g / m³: For all tests, the sorbent was dried at 120 C for 2 hours after loading 25 g of sorbent into the container. The test was performed at 24 ° C and 150 ° C operating temperature, and the amount of water in the feed benzene was changed. The feed for the test was prepared with ACN tritium in a benzene stream to produce a target of about 20 WPPm lice. The starting benzene feed was dried before it was combined with ACN. In two of the tests, the benzene feed was combined with water to determine water versus nitrogen. The results of the four failed adsorbents analysis are summarized in Table II. ,

表II 測試號碼 溫度(°C) 微量水含量 (wppm) 失效吸附劑平均 (重量%) 1 25 0 0.86 ~ 2 150 0 0.49 3 —150 50 1.07 ~ ^ 4 ~ 150 500 0.83 攸表II "丑據為在150°C範圍的升溫下,添加水到進料改進 吸附劑的氮容量。以50 wppm水、在150°C下測試,顯示比 在室溫下無水於苯進料中,約25%更大的氮容量。Table II Test No. Temperature (° C) Trace water content (wppm) Average failure adsorbent (wt%) 1 25 0 0.86 ~ 2 150 0 0.49 3 —150 50 1.07 ~ ^ 4 ~ 150 500 0.83 Table II " ugly It is believed that the addition of water to the feed improves the nitrogen capacity of the adsorbent at a temperature rise in the 150 ° C range. Tested at 50 wppm water at 150 ° C showed a nitrogen capacity of approximately 25% greater than that in anhydrous benzene feed at room temperature.

實例IV 98299.doc 200533651 來自貝例I中之測試號碼2及3的吸附劑被加以熱重力分 析(TGA),以測定在吸附劑上焦炭累積的程度。沉積在吸 附劑上的焦炭百分比及從吸附劑燃燒焦炭所需的温度,被 估計並且顯示於表爪中。Example IV 98299.doc 200533651 The adsorbents from Test Nos. 2 and 3 in Shell Example I were subjected to thermogravimetric analysis (TGA) to determine the extent of coke accumulation on the adsorbents. The percentage of coke deposited on the sorbent and the temperature required to burn the coke from the sorbent are estimated and shown in the table claw.

表III 2 8 3 <1 估計燃燒溫度(。〇 >400 <400 以TGA資料為基礎,超過4〇〇它的溫度是從來自測試號碼2 之吸附劑燃燒焦炭所須的。另外,來自測試號碼2、i 5〇〇c 且無水之吸附劑樣本的焦炭份量是約8重量%。相反地, 當溫度增加南於400°C時,來自測試號碼3之吸附劑不顯示 重大重量損失。估計是:來自在150°c&5〇 wppn^x所進行 實驗之實驗測試號碼3的此吸附劑樣本焦炭份量是低於1重 量%。因此’添加水減少在吸附劑上的焦炭形成大於 85%。當水存在於升溫下吸附腈類期間,吸附劑的再生會 較不頻繁。 【圖式簡單說明】 圖1-3描述本發明生產乙基苯的流程。 圖4-9描述本發明生產異丙苯的流程。 【主要元件符號說明】 8、10、10’、12’、14、14a-f、 管線 18、32、48,、52、52,、54、 98299.doc -39- 200533651 54’、56、56’,、58、62、66a-b、 68、68,、74、82、84、92、 100、101、102、102、102,,、 l〇4、1〇4卞、104a,M、106、 106,,,、107、110、110,、11〇ΐ、 116 、 116’ 、 116ί 、 126 、 126J 、 132、132、132’,、132…、 132卞、133 、 134 、 135 、 136 、 136J 、 142 、 142J 、 144 、 152 、 154、154,,、154卞、161、161ί、 164、164、164$、166、166,’、 166J 、 168 、 182 、 184 、 192 、 194、 20 〜30、120、120,Μ、120| 20a-c、30a-c 20d-f、30d-f、50a-50c、122a- f、122b,’,-fm 11 、 117 40 、 140 44 、 112 46 50、150、150,,、150| 58 烷化反應器 床前置空間 觸媒床 熱交換器 苯塔 習用吸附劑容器 黏土吸附劑床 轉烷化反應器 轉烷化進料管線 冷凝杰 98299.doc -40- 64 200533651 66 接收器 70 、 160 熱吸附劑容器 72、162,’、162…、162a、162b 熱吸附劑分子篩床 80 乙基苯塔 90 PEB塔 1 04a-e 進料進口管線 106a-e、106bMf-e丨” 分佈管線 124a-e、157、124a’"-e’,, 床間層空間 130 脫丙烧器塔 156、156,,、156t 轉烷化觸媒床 162 酸性分子篩吸附床 186 繞道管線 188 控制閥 190 重物塔 180 異丙苯塔 98299.doc 41Table III 2 8 3 < 1 Estimated combustion temperature (> 400 > 400 < 400 Based on TGA data, temperatures above 400 are required to burn coke from the adsorbent from test number 2. In addition, The amount of coke from the test sample No. 2, i 500c and the anhydrous adsorbent sample was about 8% by weight. Conversely, when the temperature increased by 400 ° C, the adsorbent from Test No. 3 did not show significant weight loss. It is estimated that the coke content of this adsorbent sample from the experimental test number 3 performed at 150 ° c & 50wppn ^ x is less than 1% by weight. Therefore, 'addition of water reduces coke formation on the adsorbent by more than 85%. When water is present during the adsorption of nitriles at elevated temperatures, the regeneration of the adsorbent will be less frequent. [Simplified illustration of the figure] Figure 1-3 describes the process for producing ethylbenzene according to the present invention. Figure 4-9 describes the present invention Production process of cumene. [Description of main component symbols] 8, 10, 10 ', 12', 14, 14a-f, pipelines 18, 32, 48, 52, 52, 54, 54, 98299.doc -39- 200533651 54 ', 56, 56', 58, 62, 66a-b, 68, 68, 74, 82, 84, 92 , 100, 101, 102, 102, 102 ,, 104, 104, 104a, M, 106, 106 ,,, 107, 110, 110, 110, 116, 116 ', 116ί , 126, 126J, 132, 132, 132 ', 132 ..., 132 卞, 133, 134, 135, 136, 136J, 142, 142J, 144, 152, 154, 154 ,, 154, 161, 161, 161 164, 164, 164 $, 166, 166, ', 166J, 168, 182, 184, 192, 194, 20 ~ 30, 120, 120, M, 120 | 20a-c, 30a-c 20d-f, 30d- f, 50a-50c, 122a-f, 122b, ', -fm 11, 117 40, 140 44, 112 46 50, 150, 150 ,, 150 | 58 alkylation reactor bed front space catalyst bed heat exchange Benzene tower conventional adsorbent container clay adsorbent bed transalkylation reactor transalkylation feed line condensation 98299.doc -40- 64 200533651 66 receiver 70, 160 thermal adsorbent container 72, 162, ', 162 ... , 162a, 162b Thermal adsorbent molecular sieve bed 80 Ethylbenzene column 90 PEB column 1 04a-e Feed inlet lines 106a-e, 106bMf-e 丨 "Distribution lines 124a-e, 157, 124a '" -e' , The space between the bed prop-off burner 130 156,156 ,,, 156t column alkylation catalyst bed 162 rpm acidic molecular sieve adsorbent bed 186 via line 188. Bypass control valve 190 weight cumene column 180 column 98299.doc 41

Claims (1)

200533651 、甲請專利範圍: -種從烴物流分離有機氮化 接田a , 物的方法,該方法包含: G括水及有機氮化合 哕右拖斤 的經〉可染烴物流(68,8), 該有機氮化合物包括腈類; 忒蛵物流在至少i 2〇它 ,现度下、氮吸附區域(72, 62)中與酸性分子筛接觸;及 回收除污的烴物流(丨0,23), — ^ 包括比該經污染烴物 ^更小濃度的腈類。 :請求項!的方法’其特徵在於該經污染煙物流包括芳 香族化合物。 ι· 2. 月。长項1或2的方法’其特徵在於該接觸發生在大於 12 5 c的溫度下。 士明求項1、2或3的方法,其特徵在於該經污染烴物流 中存在不多於1重量%的稀烴。 明求項1、2、3或4的方法,其特徵在於該經污染烴物 "丨L包括至少20 wppm的水。 6·如請求項1、2、3、4或5的方法,其特徵在於該除污烴 物流包括一種烴烷化基質,並且進一步包括: 將包含烷化基質及不純物的第一烷化基質進料流(12, 12’)’通過包含純化吸附劑的不純物吸附區域(46, 114), 該吸附劑包含選擇性吸附不純物的黏土或樹脂,並且從 不純物吸附區域回收經純化的烧化基質進料流(48, 48’)’其包含烷化基質,並具有的不純物濃度是低於在 弟一垸化基質進料流中的不純物濃度;及 98299.doc 200533651 將烷化劑、及至少一部份的經純化烷化基質進料流、 和至少一部份包含烴烷化基質的除污烴物流(10, 23),通 過包含烷化觸媒的烷化反應區域(20,30),以燒化劑烧化 該烷化基質,產生烷化物,並且從烷化反應區域回收含 有烷化物的反應流出流(18, 32)。 7 ·如請求項6的方法,其特徵在於至少一部份的經純化烧 化基質進料流是該經污染烴物流。 8 ·如請求項1、2、3、4或5的方法,進一步包括: 將包含烴烷化基質及有機氮化合物的烷化基質進料流 (48, 116),通到分離區域(40, 130); 從分離區域回收該經污染烴物流(68,8),其包含烴烧 化基質及有機氮化合物; 將至少一部份包含烷化基質的物流(丨2,12,),通到包 含選擇性吸附不純物之吸附劑的不純物吸附區域(46, 114) ’該不純物包含鹼性氮化合物;及 將烧化劑及至少一部份包含烧化基質的除污烴物流 (10,23)通到烧化反應區域(20,30),以烧化劑在烧化觸 媒上纟元化该烧化基質’產生烧化物,並且從烧化反應區 域回收含有烷化物的反應流出流(18, 32:)。 9·如請求項8的方法,其特徵在於該不純物吸附區域及該 氮吸附區域是與該烷化反應區域間隔的。 10.如請求項8的方法,其特徵在於來自不純物吸附區域的 流出流(48, 11 6)是該烷化基質進料流。 Π. —種烧化系統,包含: 98299.doc 200533651 一個不純物吸附容器(44,112),包含用來吸附不純物 的Ιέ 土或樹脂吸附劑(46,114),並且包括烷化基質進料 進D (12,12’)及經純化之烷化基質進料出口(48, 48,); 一個氮吸附容器(70,160),包含一個脫氮吸附劑卩2, 1 62),包含選擇性吸附氮化合物的分子篩,並且包括經 純化基質進料進口(68,161 ),與下游連通該經純化烷化 基質進料進口及脫氮烷化基質進料出口(10, i 64);及 一個烷化反應容器(20, 30),包含烷化觸媒(2〇a_f,3〇卜 f),用來在烷化條件下烷化烷化劑及烷化基質,並且包 括~個烧化反應器進口(10,18),與下游連通該脫氮烧化 基質進料出口及烷化反應出口(18, 32)。 98299.doc200533651, A. Patent scope:-A method for separating organic nitridation a from a hydrocarbon stream, the method comprising: G, including water and organic nitridation, and the right to carry the weight> the dyeable hydrocarbon stream (68, 8 ), The organic nitrogen compound includes nitriles; the hafnium stream is in contact with the acidic molecular sieve in the nitrogen adsorption zone (72, 62) at least at present, and the recovered decontaminated hydrocarbon stream (0, 23) ), — ^ Includes nitriles at a lower concentration than the contaminated hydrocarbon ^. The method of claim item! Is characterized in that the contaminated smoke stream includes an aromatic compound. ι · 2. months. The method of item 1 or 2 is characterized in that the contact occurs at a temperature greater than 12 5 c. Shi Ming's method of claim 1, 2 or 3 is characterized in that no more than 1% by weight of dilute hydrocarbons is present in the contaminated hydrocarbon stream. The method of claim 1, 2, 3 or 4, characterized in that the contaminated hydrocarbon " L includes at least 20 wppm water. 6. The method of claim 1, 2, 3, 4 or 5, characterized in that the decontaminated hydrocarbon stream comprises a hydrocarbon alkylation matrix, and further comprising: feeding a first alkylation matrix comprising an alkylation matrix and impurities. The stream (12, 12 ')' passes through an impurity adsorption region (46, 114) containing a purified adsorbent, the adsorbent comprising clay or resin that selectively adsorbs the impurity, and the purified calcined matrix feed is recovered from the impurity adsorption region Stream (48, 48 ')' which contains an alkylating matrix and has an impurity concentration that is lower than the impurity concentration in the feed stream of the primary alkylating matrix; and 98299.doc 200533651 an alkylating agent, and at least a portion Parts of a purified alkylation matrix feed stream, and at least a portion of a decontamination hydrocarbon stream (10, 23) containing a hydrocarbon alkylation matrix, through an alkylation reaction zone (20, 30) containing an alkylation catalyst to The calcining agent burns the alkylation matrix to produce an alkylate, and a reaction effluent stream containing the alkylate is recovered from the alkylation reaction zone (18, 32). 7. The method of claim 6, wherein at least a portion of the purified calcined matrix feed stream is the contaminated hydrocarbon stream. 8. The method of claim 1, 2, 3, 4 or 5, further comprising: passing an alkylation matrix feed stream (48, 116) comprising a hydrocarbon alkylation matrix and an organic nitrogen compound to a separation zone (40, 130); recovering the contaminated hydrocarbon stream (68, 8) from the separation area, which includes a hydrocarbon burning matrix and an organic nitrogen compound; passing at least a part of the stream (丨 2, 12,) containing an alkylating matrix to Impurity adsorption area (46, 114) of an adsorbent that selectively adsorbs impurities (46, 114) 'The impurity contains a basic nitrogen compound; and the calcining agent and at least a part of the decontamination hydrocarbon stream (10, 23) containing the calcination matrix are passed to the calcination In the reaction zone (20, 30), the calcination matrix is oxidized with a calcining agent on the calcination catalyst to generate a calcined product, and a reaction effluent stream containing an alkylate is recovered from the calcined reaction region (18, 32 :). 9. The method according to claim 8, wherein the impurity adsorption region and the nitrogen adsorption region are spaced from the alkylation reaction region. 10. The method of claim 8, characterized in that the effluent stream (48, 11 6) from the impurity adsorption zone is the alkylated matrix feed stream. Π. — A burning system, including: 98299.doc 200533651 an impurity adsorption container (44, 112), which contains an inorganic or resin adsorbent (46, 114) to adsorb the impurity, and includes an alkylated matrix feed and feed D (12, 12 ') and purified alkylated matrix feed outlets (48, 48,); a nitrogen adsorption vessel (70, 160), containing a denitrogen adsorbent (2, 1 62), including selective adsorption Molecular sieves of nitrogen compounds, and including a purified matrix feed inlet (68, 161), which communicates downstream with the purified alkylated matrix feed inlet and denitrified alkylation matrix feed outlet (10, i 64); and an alkyl The alkylation reaction vessel (20, 30) contains an alkylation catalyst (20a_f, 30b), which is used to alkylate the alkylating agent and the alkylation substrate under the alkylation conditions, and includes ~ a burning reactor inlet (10, 18), communicating with the downstream of the denitrification and calcination matrix feed outlet and the alkylation reaction outlet (18, 32). 98299.doc
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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112755591A (en) * 2019-10-21 2021-05-07 中国石油化工股份有限公司 Method for removing alkaline nitrogenous substances in organic solvent, method for aromatic alkylation reaction and device for aromatic alkylation reaction

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112755591A (en) * 2019-10-21 2021-05-07 中国石油化工股份有限公司 Method for removing alkaline nitrogenous substances in organic solvent, method for aromatic alkylation reaction and device for aromatic alkylation reaction
CN112755591B (en) * 2019-10-21 2023-04-07 中国石油化工股份有限公司 Method for removing alkaline nitrogenous substances in organic solvent, method for aromatic alkylation reaction and device for aromatic alkylation reaction

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