CN116059805A - A method for preparing acid gas drying dehydrating agent from waste dechlorination agent - Google Patents
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- 239000003795 chemical substances by application Substances 0.000 title claims abstract description 83
- 239000002253 acid Substances 0.000 title claims abstract description 66
- 238000001035 drying Methods 0.000 title claims abstract description 61
- 239000002699 waste material Substances 0.000 title claims abstract description 46
- 238000000034 method Methods 0.000 title claims abstract description 36
- 239000012024 dehydrating agents Substances 0.000 title claims abstract description 30
- 238000006298 dechlorination reaction Methods 0.000 title claims description 116
- 239000007789 gas Substances 0.000 claims abstract description 80
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims abstract description 50
- 239000002274 desiccant Substances 0.000 claims abstract description 39
- IXCSERBJSXMMFS-UHFFFAOYSA-N hydrogen chloride Substances Cl.Cl IXCSERBJSXMMFS-UHFFFAOYSA-N 0.000 claims abstract description 32
- 229910000041 hydrogen chloride Inorganic materials 0.000 claims abstract description 32
- 239000000463 material Substances 0.000 claims abstract description 27
- UXVMQQNJUSDDNG-UHFFFAOYSA-L Calcium chloride Chemical compound [Cl-].[Cl-].[Ca+2] UXVMQQNJUSDDNG-UHFFFAOYSA-L 0.000 claims abstract description 21
- 239000001110 calcium chloride Substances 0.000 claims abstract description 20
- 229910001628 calcium chloride Inorganic materials 0.000 claims abstract description 20
- CPLXHLVBOLITMK-UHFFFAOYSA-N magnesium oxide Inorganic materials [Mg]=O CPLXHLVBOLITMK-UHFFFAOYSA-N 0.000 claims abstract description 14
- 230000018044 dehydration Effects 0.000 claims abstract description 13
- 238000006297 dehydration reaction Methods 0.000 claims abstract description 13
- 239000000395 magnesium oxide Substances 0.000 claims abstract description 12
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N iron oxide Inorganic materials [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 claims abstract description 10
- AXZKOIWUVFPNLO-UHFFFAOYSA-N magnesium;oxygen(2-) Chemical compound [O-2].[Mg+2] AXZKOIWUVFPNLO-UHFFFAOYSA-N 0.000 claims abstract description 10
- TWNQGVIAIRXVLR-UHFFFAOYSA-N oxo(oxoalumanyloxy)alumane Chemical compound O=[Al]O[Al]=O TWNQGVIAIRXVLR-UHFFFAOYSA-N 0.000 claims abstract description 10
- NDLPOXTZKUMGOV-UHFFFAOYSA-N oxo(oxoferriooxy)iron hydrate Chemical compound O.O=[Fe]O[Fe]=O NDLPOXTZKUMGOV-UHFFFAOYSA-N 0.000 claims abstract description 10
- KKCBUQHMOMHUOY-UHFFFAOYSA-N sodium oxide Chemical compound [O-2].[Na+].[Na+] KKCBUQHMOMHUOY-UHFFFAOYSA-N 0.000 claims abstract description 10
- 229910001948 sodium oxide Inorganic materials 0.000 claims abstract description 10
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 claims abstract description 8
- 239000011575 calcium Substances 0.000 claims abstract description 8
- 229910052791 calcium Inorganic materials 0.000 claims abstract description 8
- 239000012298 atmosphere Substances 0.000 claims abstract description 7
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 24
- 230000008929 regeneration Effects 0.000 claims description 23
- 238000011069 regeneration method Methods 0.000 claims description 23
- 239000012299 nitrogen atmosphere Substances 0.000 claims description 13
- 239000000292 calcium oxide Substances 0.000 claims description 9
- ODINCKMPIJJUCX-UHFFFAOYSA-N calcium oxide Inorganic materials [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 claims description 9
- XLYOFNOQVPJJNP-UHFFFAOYSA-M hydroxide Chemical compound [OH-] XLYOFNOQVPJJNP-UHFFFAOYSA-M 0.000 claims description 8
- 239000000920 calcium hydroxide Substances 0.000 claims description 7
- 229910001861 calcium hydroxide Inorganic materials 0.000 claims description 7
- BRPQOXSCLDDYGP-UHFFFAOYSA-N calcium oxide Chemical compound [O-2].[Ca+2] BRPQOXSCLDDYGP-UHFFFAOYSA-N 0.000 claims description 7
- 239000012300 argon atmosphere Substances 0.000 claims description 3
- 238000007598 dipping method Methods 0.000 claims description 3
- 239000002245 particle Substances 0.000 claims description 3
- 239000011148 porous material Substances 0.000 claims description 3
- 230000001172 regenerating effect Effects 0.000 claims description 3
- 238000001354 calcination Methods 0.000 claims description 2
- 239000000460 chlorine Substances 0.000 abstract description 24
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 abstract description 22
- 229910052801 chlorine Inorganic materials 0.000 abstract description 22
- 238000007654 immersion Methods 0.000 abstract description 5
- 238000005406 washing Methods 0.000 abstract description 3
- 150000004679 hydroxides Chemical class 0.000 abstract description 2
- 230000000382 dechlorinating effect Effects 0.000 abstract 3
- 238000001914 filtration Methods 0.000 abstract 1
- 238000002407 reforming Methods 0.000 description 32
- 238000005516 engineering process Methods 0.000 description 19
- NLXLAEXVIDQMFP-UHFFFAOYSA-N Ammonia chloride Chemical compound [NH4+].[Cl-] NLXLAEXVIDQMFP-UHFFFAOYSA-N 0.000 description 18
- 229910052739 hydrogen Inorganic materials 0.000 description 16
- 239000001257 hydrogen Substances 0.000 description 15
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 12
- 239000003054 catalyst Substances 0.000 description 12
- 235000019270 ammonium chloride Nutrition 0.000 description 9
- 238000005260 corrosion Methods 0.000 description 9
- 230000007797 corrosion Effects 0.000 description 9
- 239000002994 raw material Substances 0.000 description 8
- 238000005984 hydrogenation reaction Methods 0.000 description 7
- 239000000047 product Substances 0.000 description 7
- 239000007787 solid Substances 0.000 description 7
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 5
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 5
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 5
- 239000003546 flue gas Substances 0.000 description 5
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 4
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 4
- 230000002378 acidificating effect Effects 0.000 description 3
- 239000003513 alkali Substances 0.000 description 3
- 238000004458 analytical method Methods 0.000 description 3
- 238000006243 chemical reaction Methods 0.000 description 3
- 150000002431 hydrogen Chemical class 0.000 description 3
- 238000004876 x-ray fluorescence Methods 0.000 description 3
- 229910052783 alkali metal Inorganic materials 0.000 description 2
- 150000001340 alkali metals Chemical class 0.000 description 2
- 229910021529 ammonia Inorganic materials 0.000 description 2
- 238000001833 catalytic reforming Methods 0.000 description 2
- 239000003610 charcoal Substances 0.000 description 2
- 238000001816 cooling Methods 0.000 description 2
- 238000011161 development Methods 0.000 description 2
- 230000018109 developmental process Effects 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000005470 impregnation Methods 0.000 description 2
- 239000012535 impurity Substances 0.000 description 2
- JEIPFZHSYJVQDO-UHFFFAOYSA-N iron(III) oxide Inorganic materials O=[Fe]O[Fe]=O JEIPFZHSYJVQDO-UHFFFAOYSA-N 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 229910052757 nitrogen Inorganic materials 0.000 description 2
- 238000005457 optimization Methods 0.000 description 2
- 238000000746 purification Methods 0.000 description 2
- 238000004064 recycling Methods 0.000 description 2
- 239000011734 sodium Substances 0.000 description 2
- 239000013589 supplement Substances 0.000 description 2
- 238000012360 testing method Methods 0.000 description 2
- WMFHUUKYIUOHRA-UHFFFAOYSA-N (3-phenoxyphenyl)methanamine;hydrochloride Chemical compound Cl.NCC1=CC=CC(OC=2C=CC=CC=2)=C1 WMFHUUKYIUOHRA-UHFFFAOYSA-N 0.000 description 1
- NIPNSKYNPDTRPC-UHFFFAOYSA-N N-[2-oxo-2-(2,4,6,7-tetrahydrotriazolo[4,5-c]pyridin-5-yl)ethyl]-2-[[3-(trifluoromethoxy)phenyl]methylamino]pyrimidine-5-carboxamide Chemical compound O=C(CNC(=O)C=1C=NC(=NC=1)NCC1=CC(=CC=C1)OC(F)(F)F)N1CC2=C(CC1)NN=N2 NIPNSKYNPDTRPC-UHFFFAOYSA-N 0.000 description 1
- 241000221988 Russula cyanoxantha Species 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 238000009825 accumulation Methods 0.000 description 1
- 239000003463 adsorbent Substances 0.000 description 1
- 150000001335 aliphatic alkanes Chemical class 0.000 description 1
- -1 ammonium ions Chemical class 0.000 description 1
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 1
- 230000003197 catalytic effect Effects 0.000 description 1
- 239000000919 ceramic Substances 0.000 description 1
- 239000007795 chemical reaction product Substances 0.000 description 1
- 150000001805 chlorine compounds Chemical class 0.000 description 1
- 230000000052 comparative effect Effects 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 238000001514 detection method Methods 0.000 description 1
- 229910001873 dinitrogen Inorganic materials 0.000 description 1
- 238000010828 elution Methods 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000001704 evaporation Methods 0.000 description 1
- 230000008020 evaporation Effects 0.000 description 1
- 238000000605 extraction Methods 0.000 description 1
- 239000002920 hazardous waste Substances 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 229910000000 metal hydroxide Inorganic materials 0.000 description 1
- 229910044991 metal oxide Inorganic materials 0.000 description 1
- 150000004706 metal oxides Chemical class 0.000 description 1
- 238000012544 monitoring process Methods 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 239000002893 slag Substances 0.000 description 1
- 238000001179 sorption measurement Methods 0.000 description 1
- 239000004575 stone Substances 0.000 description 1
- 239000002918 waste heat Substances 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/26—Drying gases or vapours
- B01D53/28—Selection of materials for use as drying agents
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2257/00—Components to be removed
- B01D2257/80—Water
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Analytical Chemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
Abstract
Description
技术领域technical field
本公开涉及干燥剂制备领域,具体地,涉及一种由废脱氯剂制备酸性气体干燥脱水剂的方法。The disclosure relates to the field of desiccant preparation, in particular to a method for preparing acid gas drying dehydrating agent from waste dechlorination agent.
背景技术Background technique
对于现代化的炼油厂,连续重整已经成为芳烃和生产高辛烷值汽油的重要技术,同时也是加氢装置用氢的主要来源,催化重整装置是否平稳运行直接影响整个炼厂的经济效益。For modern refineries, continuous reforming has become an important technology for the production of aromatics and high-octane gasoline. It is also the main source of hydrogen for hydrogenation units. The smooth operation of catalytic reforming units directly affects the economic benefits of the entire refinery.
近年重整技术尤其是连续重整发展迅速,相关的配套技术-脱氯技术是不可或缺的技术,重整装置有4个部位需采用脱氯技术,即:(1)预加氢精制石脑油的脱氯技术;(2)重整产氢气的脱氯技术;(3)重整生成油中氯的脱除技术;(4)连续重整再生单元循环再生气和放空气中氯的脱除技术。In recent years, reforming technology, especially continuous reforming, has developed rapidly, and the related supporting technology-dechlorination technology is an indispensable technology. There are 4 parts of the reforming unit that need to use dechlorination technology, namely: (1) pre-hydrogenated refined stone Naphtha dechlorination technology; (2) Dechlorination technology for reforming hydrogen production; (3) Removal technology for chlorine in reforming oil; (4) Continuous reforming regeneration unit for recycling regeneration gas and releasing chlorine in air removal technique.
重整原料需要加氢精制处理才能满足重整催化剂的要求,预加氢原料中的氯含量随原料不同有的高达150μg/g甚至更高,在预加氢反应过程中有机氯化物经加氢生成氯化氢,和预加氢过程中生成的氨反应生成氯化铵,氯化铵在低温环境下发生沉积,导致热交换、空气冷却器、水冷器低温部位的腐蚀和堵塞,为消除上述氯的影响,在预加氢反应器后增加脱氯反应器,采用固体脱氯技术,利用预加氢的反应余热,将预加氢产物中的氯化氢脱除,以保护下游装置及设备的正常运转和相关催化剂的性能。The reforming raw material needs hydrofining treatment to meet the requirements of the reforming catalyst. The chlorine content in the pre-hydrogenation raw material is as high as 150 μg/g or even higher depending on the raw material. During the pre-hydrogenation reaction, the organic chloride is hydrogenated Generate hydrogen chloride, and react with ammonia generated in the pre-hydrogenation process to generate ammonium chloride. Ammonium chloride deposits in a low-temperature environment, causing corrosion and blockage of heat exchange, air coolers, and low-temperature parts of water coolers. In order to eliminate the above-mentioned chlorine A dechlorination reactor is added after the prehydrogenation reactor, and the solid dechlorination technology is used to remove the hydrogen chloride in the prehydrogenation product by using the residual heat of the prehydrogenation reaction, so as to protect the normal operation and operation of downstream devices and equipment. performance of the associated catalyst.
对于重整装置,无论是半再生还是连续重整催化剂氯组元会不断地流失,为维持重整催化剂催化性能,在运转操作中需要不断地注入有机氯化物,进行水氯平衡控制,其催化剂流失的氯组元以氯化氢的形态存在于重整氢气和重整生成油中。这种含微量氯化氢的重整氢气在供给下游装置使用时,会带来(1)氯化氢会造成下游设备的腐蚀;(2)和微量氮结合生成氯化铵,造成冷却设备、循环压缩机堵塞、积垢,装置的安全运转存在重大隐患。同时微量氯化氢会被下游加氢装置中的催化剂吸附,影响加氢催化剂的性能,为此必须采取措施脱除重整氢中的氯化氢以消除其影响。重整氢的固体脱氯技术可以很好地解决上述问题。For the reforming unit, whether it is a semi-regenerated or continuous reforming catalyst, chlorine components will continue to be lost. In order to maintain the catalytic performance of the reforming catalyst, it is necessary to continuously inject organic chlorides during operation to control the balance of water and chlorine. The catalyst The lost chlorine components exist in reformed hydrogen and reformed oil in the form of hydrogen chloride. When this reformed hydrogen containing trace amounts of hydrogen chloride is supplied to downstream devices, it will bring (1) hydrogen chloride will cause corrosion of downstream equipment; (2) combine with trace amounts of nitrogen to form ammonium chloride, which will cause blockage of cooling equipment and circulating compressors , fouling, and there are major hidden dangers in the safe operation of the device. At the same time, a small amount of hydrogen chloride will be adsorbed by the catalyst in the downstream hydrogenation unit, which will affect the performance of the hydrogenation catalyst. Therefore, measures must be taken to remove hydrogen chloride in the reformed hydrogen to eliminate its influence. The solid dechlorination technology of reforming hydrogen can well solve the above problems.
重整生成油中氯是重整催化剂在运转过程中流失到生成油中的,含量随着重整催化剂的运转时间的增加会逐步增加,波动范围在1μg/g~4μg/g,这部分氯的存在会造成脱戊烷塔和脱丁烷塔顶冷换设备的腐蚀,当重整生成油含有较高的铵离子时,和氯化氢结合成氯化铵会在脱戊烷塔顶及脱丁烷塔顶低温部位逐渐沉积下来,积累到一定程度造成设备的堵塞,还有可能存在于重整装置的干气中会造成加热炉炉嘴的堵塞,影响重整装置的正常运转,这种情况在近年来的CCR装置中(尤其是处理量较大的装置)经常发生,另外当重整生成油作为芳烃抽提原料时,由于氯会对芳烃吸附剂的吸附性能产生影响,综上所述,需要对重整生成油采取固体脱氯技术以脱除生成油中的氯。The chlorine in the reformed oil is lost to the oil during the operation of the reforming catalyst, and the content will gradually increase with the increase of the operating time of the reforming catalyst, and the fluctuation range is 1 μg/g to 4 μg/g. The existence of the depentanizer and the debutanizer will cause corrosion of the cooling equipment at the top of the depentanizer. When the reformed oil contains high ammonium ions, it will combine with hydrogen chloride to form ammonium chloride, which will be on the top of the depentanizer and debutanizer. The low-temperature part of the top of the alkane tower is gradually deposited, and the accumulation to a certain extent will cause equipment blockage. It may also exist in the dry gas of the reforming unit, which will cause the blockage of the heating furnace nozzle and affect the normal operation of the reforming unit. In this case In recent years, it often occurs in CCR units (especially those with large processing capacity). In addition, when reformed oil is used as raw material for aromatics extraction, chlorine will affect the adsorption performance of aromatics adsorbent. In summary, , It is necessary to adopt solid dechlorination technology for the reformed oil to remove the chlorine in the oil.
无论是UOP CCR、Axens CCR还是国产CCR技术,催化剂的再生技术是其核心技术之一,在21世纪之前,连续重整装置的再生气脱氯多采用碱洗脱氯工艺,在运行过程中发现碱洗脱氯的不足之处在于设备投资大、工艺流程复杂、操作控制技术难度大、废水碱渣需要处理、设备腐蚀仍存在。2000年以后,再生气的固体脱氯技术逐渐取代了碱洗脱氯,并取到了较好的效果。Whether it is UOP CCR, Axens CCR or domestic CCR technology, catalyst regeneration technology is one of its core technologies. Disadvantages of alkali washing to remove chlorine include large equipment investment, complex process flow, difficult operation and control technology, waste water alkali slag needs to be treated, and equipment corrosion still exists. After 2000, the solid dechlorination technology of regenerated gas gradually replaced the alkali elution of chlorine, and achieved better results.
虽然固体脱氯技术用于催化重整装置有脱氯工艺简单、脱氯装置操作、监测方便、产品检测准确等特有的技术优势,但由于近年来重整装置尤其是连续重整技术发展迅速,配套的脱氯装置脱氯剂的年用量也越来越大,2020年预计脱氯剂的消耗量约为15000吨左右,由于脱氯剂属一次性使用的产品,无法通过再生得到再利用,意味着每年约有15000吨的废脱氯剂需要处置,目前常用的方法是作为危废品掩埋处理,不但掩埋处理费用巨大,同时对环境有潜在的影响,不符合石化行业绿色发展的理念。Although the solid dechlorination technology used in catalytic reforming units has unique technical advantages such as simple dechlorination process, convenient operation and monitoring of dechlorination units, and accurate product detection, due to the rapid development of reforming units, especially continuous reforming technology, in recent years, The annual consumption of dechlorination agent in the supporting dechlorination device is also increasing. In 2020, the consumption of dechlorination agent is expected to be about 15,000 tons. Since the dechlorination agent is a one-time use product, it cannot be reused through regeneration. It means that about 15,000 tons of waste dechlorination agents need to be disposed of every year. The current common method is to bury it as a hazardous waste. Not only does it cost a lot to bury it, but it also has a potential impact on the environment, which is not in line with the concept of green development in the petrochemical industry.
脱氯剂在应用过程中,由于系统腐蚀等原因使所处理的原料中含有铁锈等杂质,这些反应产物会沉积在脱氯剂上影响脱氯剂的脱氯性能以及废脱氯剂的再利用。During the application of the dechlorination agent, due to system corrosion and other reasons, the processed raw materials contain impurities such as rust, and these reaction products will be deposited on the dechlorination agent, affecting the dechlorination performance of the dechlorination agent and the reuse of the waste dechlorination agent. .
脱氯剂的脱氯原理是利用脱氯剂的结构及活性组分(比如钙)使得氯化氢吸附在脱氯剂上或和活性组分反应生成氯化物固定在脱氯剂上,所以在脱氯反应器床层中,最先和氯化氢接触的脱氯剂优先和氯化氢反应或吸附,脱氯反应属活塞式从上而下反应,由于床层下部的脱氯剂和氯化氢接触的时间减少,其脱氯性能受总体脱氯效果的限制没有完全发挥,脱氯剂中的钙等活性组分仍以部分金属氧化物或氢氧化物存在,同样会影响脱氯剂的干燥脱水性能。The dechlorination principle of the dechlorination agent is to use the structure of the dechlorination agent and the active component (such as calcium) to make hydrogen chloride adsorb on the dechlorination agent or react with the active component to form chloride and fix it on the dechlorination agent, so in dechlorination In the reactor bed, the dechlorination agent that first contacts with hydrogen chloride reacts or absorbs hydrogen chloride first, and the dechlorination reaction is a piston reaction from top to bottom. Since the contact time between the dechlorination agent and hydrogen chloride in the lower part of the bed is reduced, its The dechlorination performance is limited by the overall dechlorination effect, and the active components such as calcium in the dechlorination agent still exist as part of metal oxides or hydroxides, which will also affect the drying and dehydration performance of the dechlorination agent.
发明内容Contents of the invention
本公开的目的是将废弃的脱氯剂得到再利用,降低了废脱氯剂的处置费用和对环境的污染。The purpose of the disclosure is to reuse the waste dechlorination agent, which reduces the disposal cost of the waste dechlorination agent and the pollution to the environment.
为了实现上述目的,本公开第一方面提供一种一种由废脱氯剂制备酸性气体干燥脱水剂的方法,所述方法包括:In order to achieve the above object, the first aspect of the present disclosure provides a method for preparing an acid gas drying dehydrating agent from a waste dechlorination agent, the method comprising:
S1、将废脱氯剂在惰性气氛下进行第一焙烧处理,得到第一物料;S1. Carrying out the first roasting treatment on the waste dechlorination agent under an inert atmosphere to obtain the first material;
S2、将所述第一物料在酸液中进行浸渍处理后进行过滤洗涤,得到第二物料;S2. Dip the first material in an acid solution and then filter and wash it to obtain a second material;
S3、将所述第二物料进行干燥处理和第二焙烧处理;S3, performing drying treatment and second roasting treatment on the second material;
其中,所述废脱氯剂含有钙的氧化物和氢氧化物、氧化铝、氧化钠、氧化镁、三氧化二铁和氯化钙。Wherein, the waste dechlorination agent contains calcium oxide and hydroxide, aluminum oxide, sodium oxide, magnesium oxide, ferric oxide and calcium chloride.
可选地,以所述废脱氯剂的总重量计,钙的氧化物和氢氧化物的重量百分比为8-70wt%,氧化铝的重量百分比为30-80wt%,氧化钠的重量百分比为0.4-8wt%,氧化镁的重量百分比为0.3-2wt%,三氧化二铁的重量百分比为0.5-2wt%,氯化钙的重量百分比为20-75wt%;优选地,钙的氧化物和氢氧化物的重量百分比为10-65wt%,氧化铝的重量百分比为35-75wt%,氧化钠的重量百分比为0.5-5wt%,氧化镁的重量百分比为0.5-1.5wt%,三氧化二铁的重量百分比为1-1.6wt%,氯化钙的重量百分比为35-70wt%。Optionally, based on the total weight of the waste dechlorination agent, the weight percent of calcium oxide and hydroxide is 8-70wt%, the weight percent of aluminum oxide is 30-80wt%, and the weight percent of sodium oxide is 0.4-8wt%, the weight percent of magnesium oxide is 0.3-2wt%, the weight percent of ferric oxide is 0.5-2wt%, the weight percent of calcium chloride is 20-75wt%; preferably, the oxide of calcium and hydrogen The weight percent of oxide is 10-65wt%, the weight percent of aluminum oxide is 35-75wt%, the weight percent of sodium oxide is 0.5-5wt%, the weight percent of magnesium oxide is 0.5-1.5wt%, the weight percent of ferric oxide The weight percentage is 1-1.6 wt%, and the weight percentage of calcium chloride is 35-70 wt%.
可选地,所述惰性气氛选自氮气气氛和氩气气氛中的一种,优选为氮气气氛。Optionally, the inert atmosphere is selected from one of nitrogen atmosphere and argon atmosphere, preferably nitrogen atmosphere.
可选地,所述酸液的pH值不大于3,所述酸液选自盐酸。Optionally, the pH value of the acid solution is not greater than 3, and the acid solution is selected from hydrochloric acid.
可选地,步骤S1中,所述第一焙烧处理的条件包括:温度为450-550℃,优选为480-520℃;时间为3-6小时,优选为4-5小时;步骤S2中,所述浸渍处理的条件包括:温度为30-80℃,优选为50-60℃;时间为2-5小时,优选为3-4小时;步骤S3中,所述干燥处理的条件包括:温度为100-130℃,优选为110-120℃;时间为2-5小时,优选为3-4小时;所述第二焙烧处理的条件包括:温度为400-500℃,优选为430-450℃;时间为2-5小时,优选为3-4小时。Optionally, in step S1, the conditions of the first roasting treatment include: the temperature is 450-550°C, preferably 480-520°C; the time is 3-6 hours, preferably 4-5 hours; in step S2, The conditions of the dipping treatment include: the temperature is 30-80°C, preferably 50-60°C; the time is 2-5 hours, preferably 3-4 hours; in step S3, the conditions of the drying treatment include: the temperature is 100-130°C, preferably 110-120°C; the time is 2-5 hours, preferably 3-4 hours; the conditions of the second roasting treatment include: the temperature is 400-500°C, preferably 430-450°C; The time is 2-5 hours, preferably 3-4 hours.
本公开的第二方面提供了一种酸性气体干燥脱水剂。The second aspect of the present disclosure provides an acid gas drying and dehydrating agent.
可选地,所述酸性气体干燥脱水剂含有35-70重量%的氯化钙。Optionally, the acid gas drying and dehydrating agent contains 35-70% by weight of calcium chloride.
可选地,所述酸性气体干燥脱水剂的粒径为1-5mm,优选为2-4mm;比表面积为30-100m2/g,总孔体积为0.15-0.35cc/g。Optionally, the acid gas drying and dehydrating agent has a particle size of 1-5 mm, preferably 2-4 mm; a specific surface area of 30-100 m 2 /g, and a total pore volume of 0.15-0.35 cc/g.
本公开的第三方面提供了一种含氯化氢的酸性气体干燥脱水的方法,其特征在于,将所述酸性气体与酸性气体干燥脱水剂接触并进行脱水干燥。The third aspect of the present disclosure provides a method for drying and dehydrating acid gas containing hydrogen chloride, which is characterized in that the acid gas is contacted with an acid gas drying and dehydrating agent for dehydration and drying.
可选地所述脱水干燥的条件包括:温度为50-200℃,优选150-180℃,压力为0.1-1.0MPa,优选0.3-0.8MPa。Optionally, the dehydration and drying conditions include: a temperature of 50-200° C., preferably 150-180° C., and a pressure of 0.1-1.0 MPa, preferably 0.3-0.8 MPa.
可选地,所述方法还包括:当通过所述酸性气体干燥剂的酸性气体中水含量大于50μg/L时,对所述酸性气体干燥脱水剂进行再生;Optionally, the method further includes: when the water content in the acid gas passing through the acid gas desiccant is greater than 50 μg/L, regenerating the acid gas drying and dehydrating agent;
可选地,所述再生的条件包括:将待生的酸性气体干燥脱水剂在氮气气氛中进行焙烧;可选地,所述焙烧的温度为260~310℃。Optionally, the regeneration conditions include: roasting the acid gas drying dehydrating agent to be produced in a nitrogen atmosphere; optionally, the roasting temperature is 260-310°C.
通过上述技术方案,本公开的方法将重整脱氯装置使用后的废脱氯剂通过杂质净化处理以及组分优化后,废脱氯剂可以制备成一种酸性气体干燥脱水剂,使得废弃的脱氯剂得到重新利用,消除或降低了废脱氯剂的处置费用和对环境的污染。该干燥脱水剂可以脱除含有氯化氢的酸性气体中的水,比如可将含有1-12%水以及1-3000μg/L氯化氢的酸性气体中水脱至10-50μg/L,脱水后的气体中的氯化氢含量不变,该干燥脱水剂还具有良好的再生性能,可以重复使用。Through the above technical scheme, the disclosed method can prepare the waste dechlorination agent used by the reforming dechlorination device into an acid gas drying dehydrating agent after impurity purification treatment and component optimization, so that the waste dechlorination The chlorine agent is reused, eliminating or reducing the disposal cost of the waste dechlorination agent and the pollution to the environment. The dry dehydrating agent can remove water in acid gas containing hydrogen chloride, for example, it can remove water in acid gas containing 1-12% water and 1-3000μg/L hydrogen chloride to 10-50μg/L, and the dehydrated gas The hydrogen chloride content remains unchanged, and the dry dehydrating agent also has good regeneration performance and can be used repeatedly.
本公开的其他特征和优点将在随后的具体实施方式部分予以详细说明。Other features and advantages of the present disclosure will be described in detail in the detailed description that follows.
具体实施方式Detailed ways
以下对本公开的具体实施方式进行详细说明。应当理解的是,此处所描述的具体实施方式仅用于说明和解释本公开,并不用于限制本公开。Specific embodiments of the present disclosure will be described in detail below. It should be understood that the specific embodiments described here are only used to illustrate and explain the present disclosure, and are not intended to limit the present disclosure.
为了实现上述目的,本公开第一方面提供一种由废脱氯剂制备酸性气体干燥脱水剂的方法,所述方法包括:In order to achieve the above object, the first aspect of the present disclosure provides a method for preparing an acid gas drying dehydrating agent from a waste dechlorination agent, the method comprising:
S1、将废脱氯剂在惰性气氛下进行第一焙烧处理,得到第一物料;S1. Carrying out the first roasting treatment on the waste dechlorination agent under an inert atmosphere to obtain the first material;
S2、将所述第一物料在酸液中进行浸渍处理后进行过滤洗涤,得到第二物料;S2. Dip the first material in an acid solution and then filter and wash it to obtain a second material;
S3、将所述第二物料进行干燥处理和第二焙烧处理;S3, performing drying treatment and second roasting treatment on the second material;
其中,所述废脱氯剂含有钙的氧化物和氢氧化物、氧化铝、氧化钠、氧化镁、三氧化二铁和氯化钙。Wherein, the waste dechlorination agent contains calcium oxide and hydroxide, aluminum oxide, sodium oxide, magnesium oxide, ferric oxide and calcium chloride.
本公开的由废脱氯剂制备的酸性气体干燥剂具体的净化和组分优化方法是将废脱氯剂在氮气气氛下高温处理,将废脱氯剂吸附的油气脱除,然后在适当浓度的盐酸溶液处理去除废脱氯剂上的铁锈,于此同时盐酸和废脱氯剂中的没有和氯化氢反应的氧化钙、氢氧化钙进一步反应转化为氯化钙,经洗涤、过滤、干燥,高温下下焙烧去除氯化钙的结合水,废脱氯剂变为以无水氯化钙为主的产品,从而得到本公开的由废脱氯剂制备的酸性气体干燥剂。The specific purification and component optimization method of the acid gas desiccant prepared by the waste dechlorination agent of the present disclosure is to treat the waste dechlorination agent at high temperature under a nitrogen atmosphere, remove the oil gas adsorbed by the waste dechlorination agent, and then The hydrochloric acid solution treatment removes the iron rust on the waste dechlorination agent, and at the same time, the calcium oxide and calcium hydroxide in the hydrochloric acid and the waste dechlorination agent that do not react with hydrogen chloride are further reacted and converted into calcium chloride, which is washed, filtered, and dried. Roasting at high temperature removes the bound water of calcium chloride, and the waste dechlorination agent becomes a product mainly composed of anhydrous calcium chloride, thereby obtaining the acid gas desiccant prepared from the waste dechlorination agent of the present disclosure.
本公开所述的废脱氯剂是重整装置的固体脱氯装置脱氯剂失效后废弃的脱氯剂,包括预加氢产物高温脱氯剂、重整氢脱氯剂、重整生成油液脱氯剂以及连续重整再生单元循环再生气和放空气脱氯剂,尤其适合预加氢产物高温脱氯剂、重整装置再生烟气高温脱氯剂以及重整氢脱氯剂。The waste dechlorination agent described in this disclosure is the dechlorination agent discarded after the dechlorination agent of the solid dechlorination device of the reforming unit fails, including the high-temperature dechlorination agent of the pre-hydrogenation product, the reforming hydrogen dechlorination agent, and the reformed oil Liquid dechlorination agent and continuous reforming regeneration unit cycle regeneration gas and air dechlorination agent, especially suitable for high temperature dechlorination agent of prehydrogenation product, high temperature dechlorination agent of regenerated flue gas of reforming unit and reforming hydrogen dechlorination agent.
根据本公开,以所述废脱氯剂的总重量计,钙的氧化物和氢氧化物的重量百分比可以为8-70wt%,氧化铝的重量百分比为30-80wt%,氧化钠的重量百分比为0.4-8wt%,氧化镁的重量百分比为0.3-2wt%,三氧化二铁的重量百分比为0.5-2wt%,氯化钙的重量百分比为20-75wt%;优选地,钙的氧化物和氢氧化物的重量百分比为10-65wt%,氧化铝的重量百分比为35-75wt%,氧化钠的重量百分比为0.5-5wt%,氧化镁的重量百分比为0.5-1.5wt%,三氧化二铁的重量百分比为1-1.6wt%,氯化钙的重量百分比为35-70wt%。According to the present disclosure, based on the total weight of the waste dechlorination agent, the weight percent of calcium oxide and hydroxide can be 8-70wt%, the weight percent of aluminum oxide can be 30-80wt%, and the weight percent of sodium oxide can be 8-70wt%. 0.4-8wt%, the weight percent of magnesium oxide is 0.3-2wt%, the weight percent of ferric oxide is 0.5-2wt%, the weight percent of calcium chloride is 20-75wt%; preferably, the oxide of calcium and The weight percent of hydroxide is 10-65wt%, the weight percent of aluminum oxide is 35-75wt%, the weight percent of sodium oxide is 0.5-5wt%, the weight percent of magnesium oxide is 0.5-1.5wt%, the ferric oxide The weight percent of calcium chloride is 1-1.6wt%, and the weight percent of calcium chloride is 35-70wt%.
根据本公开,所述惰性气氛可以选自氮气气氛和氩气气氛中的一种,优选为氮气气氛。According to the present disclosure, the inert atmosphere may be selected from one of nitrogen atmosphere and argon atmosphere, preferably nitrogen atmosphere.
根据本公开,所述酸液的pH值优选不大于3,所述酸液可以选自盐酸。According to the present disclosure, the pH value of the acid solution is preferably not greater than 3, and the acid solution may be selected from hydrochloric acid.
根据本公开,步骤S1中,所述第一焙烧处理的条件包括:温度为450-550℃,优选为480-520℃;时间为3-6小时,优选为4-5小时;步骤S2中,所述浸渍处理的条件包括:温度为30-80℃,优选为50-60℃;时间为2-5小时,优选为3-4小时;步骤S3中,所述干燥处理的条件包括:温度为100-130℃,优选为110-120℃;时间为2-5小时,优选为3-4小时;所述第二焙烧处理的条件包括:温度为400-500℃,优选为430-450℃;时间为2-5小时,优选为3-4小时。According to the present disclosure, in step S1, the conditions of the first calcination treatment include: the temperature is 450-550°C, preferably 480-520°C; the time is 3-6 hours, preferably 4-5 hours; in step S2, The conditions of the dipping treatment include: the temperature is 30-80°C, preferably 50-60°C; the time is 2-5 hours, preferably 3-4 hours; in step S3, the conditions of the drying treatment include: the temperature is 100-130°C, preferably 110-120°C; the time is 2-5 hours, preferably 3-4 hours; the conditions of the second roasting treatment include: the temperature is 400-500°C, preferably 430-450°C; The time is 2-5 hours, preferably 3-4 hours.
本公开的第二方面提供了一种酸性气体干燥脱水剂。The second aspect of the present disclosure provides an acid gas drying and dehydrating agent.
根据本公开,所述酸性气体干燥脱水剂可以含有35-70重量%的氯化钙。According to the present disclosure, the acid gas drying and dehydrating agent may contain 35-70% by weight of calcium chloride.
根据本公开,所述酸性气体干燥脱水剂的粒径可以为1-5mm,优选为2-4mm;比表面积为30-100m2/g,总孔体积为0.15-0.35cc/g。According to the present disclosure, the particle size of the acid gas drying and dehydrating agent may be 1-5 mm, preferably 2-4 mm; the specific surface area is 30-100 m 2 /g, and the total pore volume is 0.15-0.35 cc/g.
本公开的酸性气体干燥剂可用于连续重整装置再生单元的循环再生气的干燥脱水工况,也可以用于其他类似气体的干燥脱水工况。The acid gas desiccant disclosed in the present disclosure can be used in the drying and dehydration working conditions of the regeneration unit of the continuous reforming device, and can also be used in the drying and dehydrating working conditions of other similar gases.
本公开的第三方面提供了一种含氯化氢的酸性气体干燥脱水的方法,其特征在于,将所述酸性气体与脱水干燥剂接触并进行脱水干燥。The third aspect of the present disclosure provides a method for drying and dehydrating an acid gas containing hydrogen chloride, which is characterized in that the acid gas is contacted with a dehydration drying agent for dehydration and drying.
根据本公开,所述脱水干燥的条件可以包括:温度为50-200℃,优选150-180℃,压力为0.1-1.0MPa,优选0.3-0.8MPa。According to the present disclosure, the dehydration and drying conditions may include: a temperature of 50-200° C., preferably 150-180° C., and a pressure of 0.1-1.0 MPa, preferably 0.3-0.8 MPa.
本公开的由废脱氯剂制备的酸性气体干燥剂可以在为50-200℃,最好在150-180℃的条件下和酸性气体接触,将再生气中的水由1-12%脱至50μg/L以下,而再生气中的氯化氢保持不变,大大降低了氯的补充,在废脱氯剂得到再利用的基础上也降低了氯的消耗,装置的环保水平提高。The acid gas desiccant prepared by the waste dechlorination agent of the present disclosure can be in contact with the acid gas at 50-200°C, preferably at 150-180°C, and remove the water in the regeneration gas from 1-12% to Below 50μg/L, while the hydrogen chloride in the regeneration gas remains unchanged, which greatly reduces the supplement of chlorine. On the basis of the reuse of the waste dechlorination agent, the consumption of chlorine is also reduced, and the environmental protection level of the device is improved.
本公开的由废脱氯剂制备的酸性气体干燥剂还具有优异的再生性能,作为本公开的一种优选的实施方式,所述方法还包括:当通过所述酸性气体干燥剂的酸性气体中水含量大于50μg/L时,对所述酸性气体干燥脱水剂进行再生。The acid gas desiccant prepared by the waste dechlorination agent of the present disclosure also has excellent regeneration performance. As a preferred embodiment of the present disclosure, the method further includes: when the acid gas passing through the acid gas desiccant When the water content is greater than 50 μg/L, the acid gas drying and dehydrating agent is regenerated.
优选地,所述再生的条件可以包括:将本公开的吸附水的酸性气体干燥剂在温度为260-310℃下,优选为290-300℃下用氮气处理,可以将吸附的水脱除,可以再利用。Preferably, the regeneration conditions may include: treating the acid gas desiccant for adsorbing water of the present disclosure with nitrogen gas at a temperature of 260-310°C, preferably 290-300°C, to remove the adsorbed water, Can be reused.
下面通过实施例来进一步说明本公开,但是本公开并不因此而受到任何限制。The present disclosure is further illustrated by the following examples, but the present disclosure is not limited thereby.
实施例1Example 1
为消除重整原料中的氯化物对下游装置的腐蚀,在预加氢反应器后串入一个脱氯反应器,利用预加氢反应的余热(温度通常在250-320℃之间),氯化氢和脱氯剂上的碱金属钙反应生成氯化钙,从而将重整原料中的氯化氢去除,同时也杜绝了氯化氢和氨反应生成氯化铵堵塞装置的现象。当脱氯反应器出口氯含量超过0.5μg/g时,脱氯罐穿透,脱氯剂需要卸除并重新装填新鲜脱氯剂再投用。取100g上述废脱氯剂,X光荧光分析(XRF)测定样品中元素含量,组成见表1。In order to eliminate the corrosion of downstream devices caused by the chloride in the reforming raw material, a dechlorination reactor is connected in series after the prehydrogenation reactor, and the hydrogen chloride It reacts with the alkali metal calcium on the dechlorination agent to generate calcium chloride, thereby removing hydrogen chloride in the reforming raw material, and also prevents the phenomenon that hydrogen chloride reacts with ammonia to generate ammonium chloride to block the device. When the chlorine content at the outlet of the dechlorination reactor exceeds 0.5 μg/g, the dechlorination tank is broken, and the dechlorination agent needs to be removed and refilled with fresh dechlorination agent before being put into use. Get 100g of above-mentioned spent dechlorination agent, X-ray fluorescence analysis (XRF) measures the element content in the sample, and composition is shown in Table 1.
将本实施例中的废脱氯剂在氮气气氛下进行第一焙烧将废脱氯剂吸附的油气脱除,得到第一物料;其中第一焙烧的条件包括:500℃高温下处理4小时降至室温;取当量浓度为0.5的盐酸溶液500毫升置于烧杯中,将第一物料慢慢加入进行浸渍处理,浸渍时间为4小时,测定溶液浓度PH值,保持PH值低于3,然后过滤、洗涤,得到第二物料;将第二物料进行干燥处理和第二焙烧处理;其中干燥处理的条件包括:在120℃干燥箱中干燥4小时,第二焙烧处理的条件包括:置于马弗炉在450℃下焙烧4小时后降至室温;本实施例制备得到的由废预加氢产物高温脱氯剂制备的酸性气体干燥剂,编号为A。The waste dechlorination agent in this example is first calcined under a nitrogen atmosphere to remove the oil gas adsorbed by the waste dechlorination agent to obtain the first material; wherein the conditions for the first roasting include: treatment at a high temperature of 500° C. for 4 hours to reduce to room temperature; take 500 ml of hydrochloric acid solution with an equivalent concentration of 0.5 and place it in a beaker, slowly add the first material for immersion treatment, the immersion time is 4 hours, measure the pH value of the solution concentration, keep the pH value below 3, and then filter , washing to obtain the second material; the second material is subjected to drying treatment and second roasting treatment; wherein the conditions of drying treatment include: drying in a 120°C drying oven for 4 hours, and the conditions of the second roasting treatment include: placing The furnace was roasted at 450° C. for 4 hours and then lowered to room temperature; the acid gas desiccant prepared from the high-temperature dechlorination agent of waste prehydrogenation product prepared in this example was designated as A.
实施例2Example 2
重整装置正常操作条件下,重整氢中含有大约1-3μg/L的氯化氢和微量的氯化铵,含有上述氯化氢和氯化铵的重整氢在重整氢循环压缩机的低温部位逐渐沉积下来,积累到一定程度造成压缩机堵塞而停车,同时氯化铵在冷凝水的作用下分解为盐酸,造成垢下腐蚀。低温脱氯工艺就是将经过再接触的重整氢串入脱氯反应器,脱氯操作温度在4-40℃之间,但受环境温度(四季温度)影响较大,通过吸附或化学反应将重整氢中的氯化氢及氯化铵脱除除,从而避免了氢循环压缩机的堵塞和腐蚀,当脱氯反应器出口氯含量超过0.5μg/L时,脱氯罐穿透,脱氯剂需要卸除并重新装填新鲜脱氯剂再投用。取100g上述废脱氯剂,X光荧光分析(XRF)测定样品中元素含量,组成见表2。Under the normal operating conditions of the reforming unit, the reformed hydrogen contains about 1-3 μg/L hydrogen chloride and a small amount of ammonium chloride, and the reformed hydrogen containing the above-mentioned hydrogen chloride and ammonium chloride gradually It is deposited and accumulated to a certain extent, causing the compressor to be blocked and shut down. At the same time, ammonium chloride is decomposed into hydrochloric acid under the action of condensed water, causing corrosion under the scale. The low-temperature dechlorination process is to string the re-contacted reformed hydrogen into the dechlorination reactor. The dechlorination operation temperature is between 4-40°C, but it is greatly affected by the ambient temperature (temperature of the four seasons). The hydrogen chloride and ammonium chloride in the reformed hydrogen are removed, thereby avoiding the blockage and corrosion of the hydrogen circulation compressor. When the chlorine content at the outlet of the dechlorination reactor exceeds 0.5 μg/L, the dechlorination tank penetrates, and the dechlorination agent It needs to be unloaded and refilled with fresh dechlorination agent before use. Get 100g of above-mentioned waste dechlorination agent, and X-ray fluorescence analysis (XRF) measures the content of elements in the sample, and the composition is shown in Table 2.
将本实施例中的废脱氯剂在氮气气氛下进行第一焙烧,将废脱氯剂吸附的油气脱除,得到第一物料;其中第一焙烧的条件包括:500℃高温下处理4小时降至室温;取当量浓度为0.2的盐酸溶液500毫升置于烧杯中,将第一物料慢慢加入进行浸渍处理,浸渍时间为静置4小时,测定溶液浓度PH值,保持PH值低于3,然后过滤、洗涤,得到第二物料;将第二物料进行干燥处理和第二焙烧处理;其中干燥处理的条件包括:在120℃干燥箱中干燥4小时,第二焙烧处理的条件包括:置于马弗炉在450℃下焙烧4小时后降至室温;本实施例制备得到的由废重整氢脱氯剂制备的酸性气体干燥剂,编号为B。Carry out the first roasting of the waste dechlorination agent in this example under a nitrogen atmosphere, remove the oil gas adsorbed by the waste dechlorination agent, and obtain the first material; wherein the conditions of the first roasting include: treatment at a high temperature of 500°C for 4 hours Cool down to room temperature; take 500 ml of hydrochloric acid solution with an equivalent concentration of 0.2 and place it in a beaker, slowly add the first material for impregnation treatment, the impregnation time is 4 hours, measure the pH value of the solution concentration, and keep the pH value below 3 , and then filtered and washed to obtain the second material; the second material is subjected to drying treatment and second roasting treatment; wherein the conditions of the drying treatment include: drying in a 120°C drying oven for 4 hours, and the conditions of the second roasting treatment include: Calcined in a muffle furnace at 450° C. for 4 hours and then lowered to room temperature; the acid gas desiccant prepared from waste reformed hydrogen dechlorination agent prepared in this example is numbered B.
实施例3Example 3
重整装置再生烟气脱氯技术包括循环再生气以及放空气的脱氯,一般情况下再生气中的氯化物大约在20μg/L到2500μg/L,为消除重整原料中的氯化物对下游装置的腐蚀影响,需设置脱氯反应器,利用再生热量余热(温度通常在200-500℃之间),氯化氢和脱氯剂上的碱金属钙反应生成氯化钙,从而将再生气中的氯化氢去除,当脱氯反应器出口氯含量超过0.5μg/g时,脱氯罐穿透,脱氯剂需要卸除并重新装填新鲜脱氯剂再投用。取100g上述废脱氯剂,X光荧光分析(XRF)测定样品中元素含量,组成见表3。The dechlorination technology of regenerative flue gas of reforming unit includes dechlorination of recycled regenerated gas and vented air. Generally, the chloride in the regenerated gas is about 20μg/L to 2500μg/L. In order to eliminate the chloride in the reforming raw material, the downstream Corrosion effect of the device, it is necessary to set up a dechlorination reactor, use the waste heat of the regeneration heat (the temperature is usually between 200-500 ℃), hydrogen chloride and the alkali metal calcium on the dechlorination agent react to generate calcium chloride, so that the regeneration gas Hydrogen chloride removal, when the chlorine content at the outlet of the dechlorination reactor exceeds 0.5 μg/g, the dechlorination tank will break through, and the dechlorination agent needs to be removed and refilled with fresh dechlorination agent before being put into use. Take 100g of the above-mentioned waste dechlorination agent, and X-ray fluorescence analysis (XRF) measures the content of elements in the sample, and the composition is shown in Table 3.
将本实施例中的废脱氯剂在氮气气氛下进行第一焙烧将废脱氯剂吸附的油气脱除,得到第一物料;其中第一焙烧的条件包括:500℃高温下处理4小时降至室温;取当量浓度为0.5的盐酸溶液500毫升置于烧杯中,将废脱氯剂慢慢加入进行浸渍处理,浸渍时间为4小时,测定溶液浓度PH值,保持PH值低于3,然后过滤、洗涤,得到第二物料;将第二物料进行干燥处理和第二焙烧处理;其中干燥处理的条件包括:在120℃干燥箱中干燥4小时,第二焙烧处理的条件包括:置于马弗炉在450℃下焙烧4小时,降至室温,;本实施例制备得到的由废再生气脱氯剂制备的酸性气体干燥剂,编号为C。The waste dechlorination agent in this example is first calcined under a nitrogen atmosphere to remove the oil gas adsorbed by the waste dechlorination agent to obtain the first material; wherein the conditions for the first roasting include: treatment at a high temperature of 500° C. for 4 hours to reduce to room temperature; take 500 milliliters of hydrochloric acid solution with an equivalent concentration of 0.5 and place it in a beaker, slowly add the waste dechlorination agent for immersion treatment, the immersion time is 4 hours, measure the pH value of the solution concentration, keep the pH value below 3, and then Filter and wash to obtain the second material; carry out drying treatment and second roasting treatment on the second material; wherein the drying treatment conditions include: drying in a 120°C drying oven for 4 hours, and the second roasting treatment conditions include: placing The furnace was fired at 450°C for 4 hours, and then lowered to room temperature; the acid gas desiccant prepared from waste regeneration gas dechlorination agent prepared in this example was designated as C.
测试例1test case 1
将100g实施例1-3得到的酸性气体干燥剂装入2端是瓷球的管状容器中,干燥氮气气氛下升温至160℃,然后通入流量为1500ml/h的酸性气体,酸性气体的组成如下:N2=88%、CO2=14%、O2=2%、H2O=6%、HCl=1500μg/L,接触过程中,气体中的水和干燥剂中的氯化钙结合成为水合氯化钙,而氯化氢不和氯化钙反应,起到脱除酸性气体中水的目的,实时测量尾气中的水含量,当水含量为50μg/L时干燥过程结束,测量各种干燥剂吸附的水含量,结果见表4。Put 100g of the acid gas desiccant obtained in Example 1-3 into a tubular container with ceramic balls at both ends, raise the temperature to 160°C under a dry nitrogen atmosphere, and then feed the acid gas with a flow rate of 1500ml/h. The composition of the acid gas As follows: N 2 = 88%, CO 2 = 14%, O 2 = 2%, H 2 O = 6%, HCl = 1500μg/L, during the contact process, the water in the gas is combined with the calcium chloride in the desiccant It becomes calcium chloride hydrate, and hydrogen chloride does not react with calcium chloride, so as to remove water from acidic gas and measure the water content in tail gas in real time. When the water content is 50μg/L, the drying process ends, and various drying The water content adsorbed by the agent is shown in Table 4.
实施例4Example 4
取测试例1中经过和酸性气体接触后的含水干燥剂A,在干燥氮气环境下,升温并控制入口温度为290℃,再生初期由于吸附的水蒸发出口温度不高,随着时间的增加,出口温度会随着干燥剂的含水量不断减少会逐渐升高,当干燥罐出口温度达到280℃时,再生结束,将反应温度降至160℃,切换实施例4中的含水酸性气体再次投用,实现干燥脱水-脱水再生循环使用。Take the water-containing desiccant A in Test Example 1 that has been in contact with acidic gas. In a dry nitrogen environment, raise the temperature and control the inlet temperature to 290°C. In the initial stage of regeneration, the outlet temperature is not high due to the evaporation of the adsorbed water. With the increase of time, The outlet temperature will gradually increase as the water content of the desiccant decreases. When the outlet temperature of the drying tank reaches 280°C, the regeneration is over, and the reaction temperature is lowered to 160°C. Switch to the acidic gas containing water in Example 4 and put it into use again. , to achieve drying dehydration - dehydration regeneration recycling.
对比例1Comparative example 1
某炼厂70万吨/年连续重整装置应用的再生烟气脱水过程:再生烟气从催化剂烧焦器出来,在0.6MPa压力、500℃温度下经过固体脱氯将再生烟气中的氯化氢脱至0.5μg/L以下,然后经过换热将再生气的温度降至40℃,在40℃工况下和干燥剂接触将再生气中的水脱至50μg/L以下,再经过电加热将温度提高至500℃,经循环压缩机返回至烧炭器中,如此循环使用,再生气用干燥剂每3天再生一次。The dehydration process of regenerated flue gas applied to a 700,000-ton/year continuous reforming unit in a refinery: the regenerated flue gas comes out of the catalyst coker, and the hydrogen chloride in the regenerated flue gas is dechlorinated by solid dechlorination at a pressure of 0.6MPa and a temperature of 500°C. Dehydrate to below 0.5μg/L, then reduce the temperature of the regeneration gas to 40°C through heat exchange, contact the desiccant at 40°C to remove the water in the regeneration gas to below 50μg/L, and then heat it up The temperature is increased to 500°C, and returned to the charcoal burner through the circulating compressor, so that it can be recycled, and the regeneration gas is regenerated every 3 days with a desiccant.
由于此干燥脱水过程需要脱氯,导致烧炭过程中催化剂的氯损失较大,需要在氧氯化步骤补充由于烧炭脱氯导致的氯损失,氯损耗较大,能耗较大。Since this drying and dehydration process requires dechlorination, the chlorine loss of the catalyst during the charcoal burning process is relatively large, and it is necessary to supplement the chlorine loss caused by charcoal dechlorination in the oxychlorination step. The chlorine loss is large and the energy consumption is large.
表1Table 1
表2Table 2
表3table 3
表4Table 4
以上详细描述了本公开的优选实施方式,但是,本公开并不限于上述实施方式中的具体细节,在本公开的技术构思范围内,可以对本公开的技术方案进行多种简单变型,这些简单变型均属于本公开的保护范围。The preferred embodiments of the present disclosure have been described in detail above, but the present disclosure is not limited to the specific details in the above embodiments. Within the scope of the technical concept of the present disclosure, various simple modifications can be made to the technical solutions of the present disclosure. These simple modifications All belong to the protection scope of the present disclosure.
另外需要说明的是,在上述具体实施方式中所描述的各个具体技术特征,在不矛盾的情况下,可以通过任何合适的方式进行组合,为了避免不必要的重复,本公开对各种可能的组合方式不再另行说明。In addition, it should be noted that the various specific technical features described in the above specific embodiments can be combined in any suitable manner if there is no contradiction. The combination method will not be described separately.
此外,本公开的各种不同的实施方式之间也可以进行任意组合,只要其不违背本公开的思想,其同样应当视为本公开所公开的内容。In addition, various implementations of the present disclosure can be combined arbitrarily, as long as they do not violate the idea of the present disclosure, they should also be regarded as the content disclosed in the present disclosure.
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