JPH0747750B2 - Method for removing mercury in liquid hydrocarbons - Google Patents
Method for removing mercury in liquid hydrocarbonsInfo
- Publication number
- JPH0747750B2 JPH0747750B2 JP3110709A JP11070991A JPH0747750B2 JP H0747750 B2 JPH0747750 B2 JP H0747750B2 JP 3110709 A JP3110709 A JP 3110709A JP 11070991 A JP11070991 A JP 11070991A JP H0747750 B2 JPH0747750 B2 JP H0747750B2
- Authority
- JP
- Japan
- Prior art keywords
- mercury
- adsorbent
- sulfide
- gas
- liquid hydrocarbons
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Lifetime
Links
- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 title claims description 64
- 229910052753 mercury Inorganic materials 0.000 title claims description 57
- 239000007788 liquid Substances 0.000 title claims description 26
- 229930195733 hydrocarbon Natural products 0.000 title claims description 16
- 150000002430 hydrocarbons Chemical class 0.000 title claims description 16
- 238000000034 method Methods 0.000 title claims description 14
- 239000003463 adsorbent Substances 0.000 claims description 37
- UCKMPCXJQFINFW-UHFFFAOYSA-N Sulphide Chemical compound [S-2] UCKMPCXJQFINFW-UHFFFAOYSA-N 0.000 claims description 15
- 229910001385 heavy metal Inorganic materials 0.000 claims description 7
- CWQXQMHSOZUFJS-UHFFFAOYSA-N molybdenum disulfide Chemical compound S=[Mo]=S CWQXQMHSOZUFJS-UHFFFAOYSA-N 0.000 claims description 6
- 239000004215 Carbon black (E152) Substances 0.000 claims description 5
- 229910017313 Mo—Co Inorganic materials 0.000 claims 1
- 229910017318 Mo—Ni Inorganic materials 0.000 claims 1
- 229910017709 Ni Co Inorganic materials 0.000 claims 1
- 229910003267 Ni-Co Inorganic materials 0.000 claims 1
- 229910003262 Ni‐Co Inorganic materials 0.000 claims 1
- 238000010438 heat treatment Methods 0.000 description 22
- 239000003498 natural gas condensate Substances 0.000 description 14
- 239000007789 gas Substances 0.000 description 11
- 238000001179 sorption measurement Methods 0.000 description 11
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 description 10
- 230000000052 comparative effect Effects 0.000 description 7
- 230000000694 effects Effects 0.000 description 6
- 229910052759 nickel Inorganic materials 0.000 description 6
- 229910018072 Al 2 O 3 Inorganic materials 0.000 description 5
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 5
- 229910017052 cobalt Inorganic materials 0.000 description 5
- 239000010941 cobalt Substances 0.000 description 5
- GUTLYIVDDKVIGB-UHFFFAOYSA-N cobalt atom Chemical compound [Co] GUTLYIVDDKVIGB-UHFFFAOYSA-N 0.000 description 5
- 238000005987 sulfurization reaction Methods 0.000 description 5
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 4
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 4
- -1 natural gas Chemical class 0.000 description 4
- ZOKXTWBITQBERF-UHFFFAOYSA-N Molybdenum Chemical compound [Mo] ZOKXTWBITQBERF-UHFFFAOYSA-N 0.000 description 3
- 238000009835 boiling Methods 0.000 description 3
- 239000012159 carrier gas Substances 0.000 description 3
- 239000011521 glass Substances 0.000 description 3
- 229910052751 metal Inorganic materials 0.000 description 3
- 239000002184 metal Substances 0.000 description 3
- 229910052750 molybdenum Inorganic materials 0.000 description 3
- 239000011733 molybdenum Substances 0.000 description 3
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 2
- 238000000354 decomposition reaction Methods 0.000 description 2
- 239000006185 dispersion Substances 0.000 description 2
- 238000004821 distillation Methods 0.000 description 2
- 239000003345 natural gas Substances 0.000 description 2
- 239000003921 oil Substances 0.000 description 2
- 239000002994 raw material Substances 0.000 description 2
- 239000000243 solution Substances 0.000 description 2
- 229910052720 vanadium Inorganic materials 0.000 description 2
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 1
- VGGSQFUCUMXWEO-UHFFFAOYSA-N Ethene Chemical compound C=C VGGSQFUCUMXWEO-UHFFFAOYSA-N 0.000 description 1
- 239000005977 Ethylene Substances 0.000 description 1
- 229910003296 Ni-Mo Inorganic materials 0.000 description 1
- 229910018198 Ni—Co—M Inorganic materials 0.000 description 1
- 229910021536 Zeolite Inorganic materials 0.000 description 1
- HSFWRNGVRCDJHI-UHFFFAOYSA-N alpha-acetylene Natural products C#C HSFWRNGVRCDJHI-UHFFFAOYSA-N 0.000 description 1
- 239000007864 aqueous solution Substances 0.000 description 1
- 239000003054 catalyst Substances 0.000 description 1
- 239000000919 ceramic Substances 0.000 description 1
- 239000013064 chemical raw material Substances 0.000 description 1
- 239000002131 composite material Substances 0.000 description 1
- 230000007797 corrosion Effects 0.000 description 1
- 238000005260 corrosion Methods 0.000 description 1
- 239000010779 crude oil Substances 0.000 description 1
- 239000013078 crystal Substances 0.000 description 1
- 230000006866 deterioration Effects 0.000 description 1
- 150000001993 dienes Chemical class 0.000 description 1
- 229910001873 dinitrogen Inorganic materials 0.000 description 1
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 description 1
- 125000002534 ethynyl group Chemical group [H]C#C* 0.000 description 1
- 238000001704 evaporation Methods 0.000 description 1
- 230000008020 evaporation Effects 0.000 description 1
- 239000011261 inert gas Substances 0.000 description 1
- 239000003350 kerosene Substances 0.000 description 1
- 150000002730 mercury Chemical class 0.000 description 1
- 229940100892 mercury compound Drugs 0.000 description 1
- 150000002731 mercury compounds Chemical class 0.000 description 1
- 229910052976 metal sulfide Inorganic materials 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 239000003595 mist Substances 0.000 description 1
- 239000002808 molecular sieve Substances 0.000 description 1
- DDTIGTPWGISMKL-UHFFFAOYSA-N molybdenum nickel Chemical compound [Ni].[Mo] DDTIGTPWGISMKL-UHFFFAOYSA-N 0.000 description 1
- 229910000476 molybdenum oxide Inorganic materials 0.000 description 1
- 238000010943 off-gassing Methods 0.000 description 1
- 238000012805 post-processing Methods 0.000 description 1
- 238000000197 pyrolysis Methods 0.000 description 1
- 239000011347 resin Substances 0.000 description 1
- 229920005989 resin Polymers 0.000 description 1
- 102200118166 rs16951438 Human genes 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 239000000377 silicon dioxide Substances 0.000 description 1
- 238000005245 sintering Methods 0.000 description 1
- URGAHOPLAPQHLN-UHFFFAOYSA-N sodium aluminosilicate Chemical compound [Na+].[Al+3].[O-][Si]([O-])=O.[O-][Si]([O-])=O URGAHOPLAPQHLN-UHFFFAOYSA-N 0.000 description 1
- HYHCSLBZRBJJCH-UHFFFAOYSA-N sodium polysulfide Chemical compound [Na+].S HYHCSLBZRBJJCH-UHFFFAOYSA-N 0.000 description 1
- 229910052979 sodium sulfide Inorganic materials 0.000 description 1
- GRVFOGOEDUUMBP-UHFFFAOYSA-N sodium sulfide (anhydrous) Chemical compound [Na+].[Na+].[S-2] GRVFOGOEDUUMBP-UHFFFAOYSA-N 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 150000004763 sulfides Chemical class 0.000 description 1
- WFKWXMTUELFFGS-UHFFFAOYSA-N tungsten Chemical compound [W] WFKWXMTUELFFGS-UHFFFAOYSA-N 0.000 description 1
- 229910052721 tungsten Inorganic materials 0.000 description 1
- 239000010937 tungsten Substances 0.000 description 1
- LEONUFNNVUYDNQ-UHFFFAOYSA-N vanadium atom Chemical compound [V] LEONUFNNVUYDNQ-UHFFFAOYSA-N 0.000 description 1
- 239000010457 zeolite Substances 0.000 description 1
Landscapes
- Treating Waste Gases (AREA)
- Separation Of Gases By Adsorption (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
- Production Of Liquid Hydrocarbon Mixture For Refining Petroleum (AREA)
Description
【0001】[0001]
【産業上の利用分野】液状炭化水素、例えば天然ガスよ
り回収されるNGL(天然ガスコンデンセート)中には
産地により数十〜数百ppbに達する水銀が含まれてい
る。NGLを化学原料として使う分野、例えばエチレン
原料として使う場合、深冷分離工程の熱交換器の腐蝕、
アセチレン、ジエン等を水添する工程の触媒の劣化が問
題になる。天然ガスなどガス状炭化水素中の水銀除去に
ついては、すでに硫黄担持活性炭などが使われている
が、液状炭化水素についてはまだ工業化されたプロセス
がない。BACKGROUND OF THE INVENTION Liquid hydrocarbons, such as NGL (natural gas condensate) recovered from natural gas, contain tens to hundreds of ppb of mercury depending on the place of origin. When NGL is used as a chemical raw material, for example, as an ethylene raw material, corrosion of the heat exchanger in the cryogenic separation process,
The deterioration of the catalyst in the step of hydrogenating acetylene, diene, etc. becomes a problem. For removing mercury in gaseous hydrocarbons such as natural gas, sulfur-supporting activated carbon has already been used, but for liquid hydrocarbons, there is no industrialized process.
【0002】[0002]
【従来の技術】本発明者らは、水銀を含有する液又はガ
スを、モリブデン、タングステン及びバナジウムよりな
る群から選ばれる一種又は二種以上の金属の硫化物を含
有する吸着剤に接触させることを特徴とする水銀の除去
方法(特開平2-2873)を提案した。BACKGROUND OF THE INVENTION The inventors of the present invention contact a liquid or gas containing mercury with an adsorbent containing a sulfide of one or more metals selected from the group consisting of molybdenum, tungsten and vanadium. A method for removing mercury (Japanese Patent Laid-Open No. 2-2873) was proposed.
【0003】しかしNGLには単体水銀のほかにイオン
状水銀や有機水銀が含まれている。上記のような重金属
硫化物からなる吸着剤は単体水銀の除去には有効である
が、イオン状水銀や高分子量の有機水銀の除去に関して
はあまり有効ではない。イオン状水銀や高分子量の有機
水銀も除去するために硫化ソーダ、ポリ硫化ソーダなど
の水溶液と接触させて吸収させる手段を併用する方法も
有効であるが、プロセス的に複雑になることは避けられ
ない。However, NGL contains ionic mercury and organic mercury in addition to elemental mercury. Although the adsorbents composed of heavy metal sulfides as described above are effective in removing elemental mercury, they are not so effective in removing ionic mercury and high molecular weight organic mercury. In order to remove ionic mercury and high molecular weight organic mercury, it is also effective to use a method of contacting with an aqueous solution such as sodium sulfide or sodium polysulfide to absorb it, but it is possible to avoid complication in the process. Absent.
【0004】[0004]
【発明が解決しようとする課題】本発明は、各種形態の
水銀を含有する液状炭化水素、例えば、灯油、軽油、直
留ナフサ、減圧留出油等の原油または天然ガスコンデン
セート(NGL)留分、熱分解ガソリン、接触分解ナフ
サ等の分解生成油、天然ガスコンデンセート等から、簡
単な操作で水銀を除去する方法を提供することを目的と
する。The present invention is directed to liquid hydrocarbons containing various forms of mercury, for example, crude oil such as kerosene, light oil, straight run naphtha, vacuum distillate or natural gas condensate (NGL) fraction. An object of the present invention is to provide a method for removing mercury from pyrolysis gasoline, cracked oil such as catalytically cracked naphtha, natural gas condensate and the like by a simple operation.
【0005】[0005]
【課題を解決するための手段】本発明による液状炭化水
素中の水銀除去法は、水銀を含有する液状炭化水素を9
0℃以上の温度で加熱処理して蒸発させ、得られるガス
状成分をガス状のまま重金属硫化物を含む吸着剤に接触
させることを特徴とする。The method for removing mercury in liquid hydrocarbons according to the present invention is a method for removing mercury containing liquid hydrocarbons.
It is characterized in that a gaseous component obtained by heat treatment at a temperature of 0 ° C. or higher is vaporized, and the obtained gaseous component is brought into contact with an adsorbent containing a heavy metal sulfide in a gaseous state.
【0006】原料液状炭化水素中のイオン状水銀や高分
子量の有機水銀は90℃以上の温度で分解し始めて単体
水銀(元素状水銀)の形態に変化して行き、200℃以
上では殆ど完全に分解する。加熱温度が200℃未満で
イオン状水銀や高分子量の有機水銀の分解率が低い場合
でも、未分解のものは液中にとどまり、蒸発したガス状
成分に同伴されるのは殆どが単体水銀なので、ガス状成
分をそのまま重金属硫化物を含む吸着剤に接触させれば
大部分の水銀が除去されることがわかった。なおガス状
成分の取得率と言う点からは、液状炭化水素の種類にも
よるが、一般に250℃以上に加熱することが望まし
い。加熱処理温度の上限は対象炭化水素の分解温度以下
とすべきは当然であり、370℃前後を上限とする。加
熱処理時のLHSVは0.1〜100hr-1、実用的に
は1〜50hr-1とするのが好ましい。Ionic mercury and high molecular weight organic mercury in the raw liquid hydrocarbons start to decompose at a temperature of 90 ° C. or higher and change to the form of elemental mercury (elemental mercury), and at 200 ° C. or higher, almost completely. Disassemble. Even if the heating temperature is less than 200 ° C and the decomposition rate of ionic mercury or high-molecular weight organic mercury is low, undecomposed matter remains in the liquid and most of the mercury that accompanies the vaporized gaseous components is elemental mercury. It was found that most of the mercury was removed by contacting the gaseous component as it was with the adsorbent containing heavy metal sulfide. From the viewpoint of the acquisition rate of the gaseous component, it is generally desirable to heat it to 250 ° C. or higher, although it depends on the type of liquid hydrocarbon. The upper limit of the heat treatment temperature should be lower than the decomposition temperature of the target hydrocarbon, and the upper limit is around 370 ° C. LHSV at the time of heat treatment is preferably 0.1 to 100 hr -1 , and practically 1 to 50 hr -1 .
【0007】重金属硫化物を含む吸着剤としてはCu,
V,W等の硫化物を含む吸着剤を使用することも可能で
あるが、モリブデンの硫化物を主体とするものが好まし
い。モリブデンの硫化物は極めて高い単体水銀吸着活性
を有しているが、モリブデンの硫化物による水銀の吸着
効果をさらに向上させるためには、コバルト及び/又は
ニッケルと組み合わせ複合硫化物として用いるのが有効
である。コバルト及び/又はニッケルはモリブデンの酸
化物を硫化する際に、より低温で硫化を開始させると同
時に、コバルト及び/又はニッケルがモリブデンの硫化
物の結晶にとりこまれてそのシンタリングが防止され、
その結果高分散の硫化物が得られるという効果を与え
る。コバルト及び/又はニッケルの含有量はモリブデン
1原子に対して0.05〜0.9原子、好ましくは0.
1〜0.8原子であることが望ましい。原子比0.05
以下では分散化の効果が小さく、一方0.9以上に増し
ても効果はそれほど上がらない。As the adsorbent containing heavy metal sulfide, Cu,
Although it is possible to use an adsorbent containing a sulfide such as V or W, one mainly containing a sulfide of molybdenum is preferable. Molybdenum sulfide has an extremely high activity of adsorbing mercury as a simple substance, but it is effective to use it as a composite sulfide in combination with cobalt and / or nickel to further improve the mercury adsorption effect of molybdenum sulfide. Is. When cobalt and / or nickel sulfides molybdenum oxide, it initiates sulfide at a lower temperature, and at the same time cobalt and / or nickel is incorporated into molybdenum sulfide crystals to prevent sintering.
As a result, a highly dispersed sulfide is obtained. The content of cobalt and / or nickel is 0.05 to 0.9 atom based on 1 atom of molybdenum, preferably 0.
It is preferably 1 to 0.8 atoms. Atomic ratio 0.05
In the following, the effect of dispersion is small, but even if it is increased to 0.9 or more, the effect does not increase so much.
【0008】これら金属の硫化物はそのままで吸着剤と
して用いることもできるが、吸着剤を担体に担持させて
用いると吸着剤の分散度が向上し、単に吸着量を増加さ
せるのみならず、吸着速度も増加し、単体水銀以外の水
銀も有効に除去できるので、担体に坦持させて用いるの
が好ましい。担体としてはシリカ、アルミナ、シリカ−
アルミナ、ゼオライト、セラミック、ガラス、樹脂又は
活性炭などを用いることができるが、特にアルミナに吸
着させた吸着剤は分散性が高く、本発明の吸着剤として
優れている。アルミナの中では特にγ−アルミナが好適
である。These metal sulfides can be used as an adsorbent as they are, but when the adsorbent is carried on a carrier, the dispersibility of the adsorbent is improved, and not only the adsorption amount is increased but also the adsorption amount is increased. Since the speed is increased and mercury other than elemental mercury can be effectively removed, it is preferable to use it by supporting it on a carrier. As the carrier, silica, alumina, silica-
Alumina, zeolite, ceramics, glass, resin, activated carbon, or the like can be used. Particularly, the adsorbent adsorbed on alumina has high dispersibility and is excellent as the adsorbent of the present invention. Of the alumina, γ-alumina is particularly preferable.
【0009】担体に担持させる場合、モリブデンの硫化
物の担持量は金属として1〜20wt%、特に5〜15
wt%の範囲が好ましい。担持量がこれ以上になると担
体の効果が小さく分散が悪くなる。また担持量が少ない
場合には吸着剤あたりの吸着量が小さくなる。コバルト
及び/又はニッケルを添加した場合、その添加量は吸着
剤に対して金属として0.1〜5wt%であることが好
ましい。When supported on a carrier, the supported amount of molybdenum sulfide is 1 to 20 wt% as metal, especially 5 to 15%.
A range of wt% is preferred. If the amount supported is greater than this, the effect of the carrier is small and the dispersion becomes poor. Further, when the supported amount is small, the adsorbed amount per adsorbent becomes small. When cobalt and / or nickel is added, the addition amount is preferably 0.1 to 5 wt% as a metal with respect to the adsorbent.
【0010】担体は比表面積が大きいものの方が接触効
率が良くなるので好ましく、5〜400m2 /g、特に
100〜250m2 /gの比表面積を有するものが好ま
しいが、これらに限定されるものではない。[0010] What support preferably so better things large specific surface area the better the contact efficiency, 5~400m 2 / g, particularly preferably those having a specific surface area of 100 to 250 m 2 / g, which is limited to is not.
【0011】水銀を含有する液状炭化水素と吸着剤との
接触方法は任意であるが、特に固定床流通方式が好まし
い。固定床流通方式を採用することにより連続運転が可
能となる。The method of contacting the liquid hydrocarbon containing mercury with the adsorbent is arbitrary, but the fixed bed flow system is particularly preferable. Continuous operation is possible by adopting the fixed bed distribution method.
【0012】吸着の際の温度条件は蒸発したガス状成分
の液化を防ぐに必要な温度以上、すなわち加熱温度と同
じか、それより若干(5〜10℃)高い温度とする。G
HSVは10〜10,000hr-1、実用的には100
〜5,000hr-1とするのが好ましい。The temperature condition for the adsorption is not lower than the temperature required to prevent the liquefaction of the vaporized gaseous component, that is, the same as or slightly higher than the heating temperature (5 to 10 ° C.). G
HSV is 10 to 10,000 hr -1 , practically 100
It is preferably set to 5,000 hr -1 .
【0013】以下実施例により本発明を具体的に説明
し、比較例と対比する。The present invention will be specifically described below with reference to examples, and will be compared with comparative examples.
【0014】[0014]
【比較例1】水銀及び水銀化合物を800ppb(水銀
として)含有する天然ガスコンデンセート10mlを加
熱することなくそのまま容量30mlのガラス瓶に入
れ、あらかじめ硫化したCo−Mo系吸着剤(硫化前の
Mo含有量:7重量%,Co含有量:0.9重量%,担
体:γ−Al2 O3 ,60〜80メッシュ)50mgを
加えて30分間振盪後液中の水銀を分析したところ水銀
としての濃度は630ppbであった。この結果、この
天然ガスコンデンセート中の水銀は大部分が吸着剤で吸
着されない有機水銀又はイオン状水銀の形態であること
が判明した。[Comparative Example 1] 10 ml of natural gas condensate containing 800 ppb (as mercury) of mercury and a mercury compound was directly placed in a glass bottle having a capacity of 30 ml without heating, and a pre-sulfurized Co-Mo-based adsorbent (Mo content before sulfurization) : 7% by weight, Co content: 0.9% by weight, carrier: γ-Al 2 O 3 , 60-80 mesh) 50 mg, and after shaking for 30 minutes, the mercury in the solution was analyzed. It was 630 ppb. As a result, it was found that most of the mercury in the natural gas condensate was in the form of organic mercury or ionic mercury that was not adsorbed by the adsorbent.
【0015】[0015]
【実施例1】長さ200mm、内径8mmのSUS30
4製加熱管に2mm径のSUSボールを80mm高さま
で充填した装置を使用し、比較例1で用いた水銀を80
0ppb(μg/l)含有する天然ガスコンデンセート
を予熱して所定温度に保たれた加熱管充填層上部表面に
0.6ml/分の一定流量で導入した。このときキャリ
アーとして不活性ガスである窒素ガスを2.3ml/分
の流量でアップフローで流した。重質分は加熱管下方よ
り液のまま抜き出すようにした。加熱管下流側に内径8
mmのSUS304製吸着管を設け、吸着剤1.4gを
充填した。吸着剤は予め硫化したCo−Mo系吸着剤
(硫化前のMo含有量:7.0%,Co含有量:0.9
%,担体:γ−Al2 O3 ,60〜80メッシュ)を用
いた。温度は加熱管と同一または僅かに高くなるように
加熱した。加熱管と吸着管の接続配管もすべて加熱管と
同じ温度に保持し、蒸発液の凝縮が起こらないようにし
た。加熱管上部から流出したガス状成分を吸着管に導入
して吸着剤と接触させ、吸着管出口ガスは空冷した後気
液分離器を通し、気液分離器で分離された留出液と留出
ガスの水銀分析結果を表1に示した。表1より、加熱処
理を行うことにより天然ガスコンデンセート中の水銀は
吸着剤で効果的に除去できることがわかる。特に220
℃以下では完全に除去されている。250℃以上では僅
かに水銀が流出しているが、これは十分に加熱されてい
ないミストが加熱管上部からキャリアーガスに同伴さ
れ、これにより難吸着性の水銀が残存していたか、ある
いは吸着剤から水銀の一部が放散したものと考えられ
る。Example 1 SUS30 having a length of 200 mm and an inner diameter of 8 mm
Using a device in which a heating tube made of No. 4 was filled with SUS balls having a diameter of 2 mm to a height of 80 mm, the mercury used in Comparative Example 1 was added to 80
Natural gas condensate containing 0 ppb (μg / l) was preheated and introduced at a constant flow rate of 0.6 ml / min onto the upper surface of the heating tube packed bed kept at a predetermined temperature. At this time, nitrogen gas, which is an inert gas, was used as a carrier at an upflow rate of 2.3 ml / min. The heavy components were extracted from the lower part of the heating tube as liquid. Inner diameter 8 on the downstream side of the heating tube
A SUS304 adsorption tube of mm was provided and 1.4 g of the adsorbent was filled. The adsorbent was a pre-sulfurized Co-Mo adsorbent (Mo content before sulfurization: 7.0%, Co content: 0.9
%, Carrier: γ-Al 2 O 3 , 60 to 80 mesh) was used. The heating temperature was the same as or slightly higher than that of the heating tube. All the connecting pipes of the heating pipe and the adsorption pipe were kept at the same temperature as that of the heating pipe to prevent the evaporation liquid from condensing. The gaseous component flowing out from the upper part of the heating tube is introduced into the adsorption tube and brought into contact with the adsorbent.The adsorption tube outlet gas is air-cooled and then passed through the gas-liquid separator, and the distillate separated by the gas-liquid separator The results of mercury analysis of the outgassing are shown in Table 1. It can be seen from Table 1 that the mercury in the natural gas condensate can be effectively removed by the adsorbent by performing the heat treatment. Especially 220
It is completely removed below ℃. At 250 ° C or higher, a small amount of mercury flows out, but this is because mist that is not sufficiently heated is entrained in the carrier gas from the upper part of the heating tube, and as a result, mercury that is difficult to adsorb remains, or the adsorbent Therefore, it is considered that some of the mercury was released.
【表1】 [Table 1]
【0016】[0016]
【比較例2】吸着管を用いない以外は実施例1と同じ条
件で加熱処理試験を行った。気液分離器で分離された留
出液と留出ガスの水銀分析結果を表2に示した。原料の
天然ガスコンデンセート中に含まれる水銀量は4.8μ
g(6ml×800ppb)であるので、ガス側には4
8〜73%の水銀が流出していることがわかる。この水
銀は大部分が元素状水銀に変化しており、実施例1のご
とく吸着剤により吸着される。Comparative Example 2 A heat treatment test was conducted under the same conditions as in Example 1 except that the adsorption tube was not used. Table 2 shows the mercury analysis results of the distillate and the distillate gas separated by the gas-liquid separator. The amount of mercury contained in the raw material natural gas condensate is 4.8μ.
Since it is g (6 ml x 800 ppb), it is 4 on the gas side.
It can be seen that 8 to 73% of mercury is flowing out. Most of this mercury is changed to elemental mercury and is adsorbed by the adsorbent as in Example 1.
【表2】 [Table 2]
【0017】[0017]
【実施例2】全水銀167ppb(μg/l)を含有す
る天然ガスコンデンセートを、実施例1と同様にして加
熱処理して蒸発させた。コンデンセート流量は0.6m
l/分、キャリヤーガス流量は2.3ml/分とした。
吸着管には予め硫化したCo−Mo系吸着剤(硫化前の
Mo含有量:7.0%,Co含有量:0.9%,担体:
γ−Al2 O3 ,60〜80メッシュ)を1.5g充填
した。加熱管と吸着管の加熱温度は240℃に設定し
た。この時の気液分離器で分離された留出液と留出ガス
の水銀分析結果を表3に示した。Example 2 A natural gas condensate containing 167 ppb (μg / l) of total mercury was heat-treated and evaporated in the same manner as in Example 1. Condensate flow rate is 0.6m
The flow rate of the carrier gas was set at 1 / min and the carrier gas flow rate was set at 2.3 ml / min.
A pre-sulfurized Co-Mo-based adsorbent (Mo content before sulfuration: 7.0%, Co content: 0.9%, carrier:
γ-Al 2 O 3, 60 to 80 mesh) was 1.5g filled. The heating temperature of the heating tube and the adsorption tube was set to 240 ° C. Table 3 shows the mercury analysis results of the distillate and the distillate gas separated by the gas-liquid separator at this time.
【0018】[0018]
【実施例3】吸着剤として予め硫化したNi−Mo系吸
着剤(硫化前のMo含有量:6.9%,Ni含有量:
1.2%,担体:γ−Al2 O3,60〜80メッシ
ュ)1.5gを使用した以外は、実施例2と同様な試験
を行った。この時の気液分離器で分離された留出液と留
出ガスの水銀分析結果を表3に示した。Example 3 A pre-sulfurized Ni-Mo adsorbent as an adsorbent (Mo content before sulfurization: 6.9%, Ni content:
The same test as in Example 2 was conducted except that 1.5 g of 1.2%, carrier: γ-Al 2 O 3 , 60 to 80 mesh) was used. Table 3 shows the mercury analysis results of the distillate and the distillate gas separated by the gas-liquid separator at this time.
【0019】[0019]
【実施例4】吸着剤として予め硫化したNi−Co−M
o系吸着剤(硫化前のMo含有量:6.7%,Co含有
量:0.9%,Ni含有量:0.5%,担体:γ−Al
2 O3 ,60〜80メッシュ)1.5gを使用した以外
は、実施例2と同様な試験を行った。この時の気液分離
器で分離された留出液と留出ガスの水銀分析結果を表3
に示した。Example 4 Pre-sulfidized Ni-Co-M as adsorbent
o-based adsorbent (Mo content before sulfurization: 6.7%, Co content: 0.9%, Ni content: 0.5%, carrier: γ-Al
2 O 3 , 60 to 80 mesh) The same test as in Example 2 was performed except that 1.5 g was used. Table 3 shows the mercury analysis results of the distillate and the distillate gas separated by the gas-liquid separator at this time.
It was shown to.
【0020】[0020]
【比較例3】吸着管に吸着剤を充填せずに、実施例2と
同様な試験を行った。この時の気液分離器で分離された
留出液と留出ガスの水銀分析結果を表3に示した。Comparative Example 3 The same test as in Example 2 was conducted without filling the adsorbent tube with the adsorbent. Table 3 shows the mercury analysis results of the distillate and the distillate gas separated by the gas-liquid separator at this time.
【0021】表3より、水銀を含有する液状炭化水素を
90℃以上の温度で加熱処理して蒸発させ、得られるガ
ス状成分をガス状のまま重金属硫化物を含む吸着剤に接
触させた場合、蒸発ガス側では水銀の除去率は原料コン
デンセートに対して96%以上になることが分かる。し
かし吸着剤を使用しない場合(比較例3)はこのコンデ
ンセート中の水銀はガス側に72%流出している。According to Table 3, when a liquid hydrocarbon containing mercury is heat-treated at a temperature of 90 ° C. or higher to be evaporated, and the obtained gaseous component is brought into contact with an adsorbent containing a heavy metal sulfide in a gaseous state. , it is understood to be a removal rate of mercury than 96 percent versus the raw condensate is evaporated gas side. However, when no adsorbent was used (Comparative Example 3), 72% of the mercury in the condensate flowed out to the gas side.
【表3】 [Table 3]
【0022】[0022]
【実施例5】水銀をほとんど含まない天然ガスコンデン
セート(初期沸点35℃、50%留出温度134.5
℃、最終沸点367℃)にジイソプロピルメルカプト水
銀を添加して水銀濃度950ppb(μg/l)のモデ
ル液を調製した。この液を0.3〜0.5mm径にそろ
えたモレキュラーシーブ3Aを30cm長さに充填した
ガラスカラム(内径4mm)に定量ポンプで2ml/分
の流速で通液した。このとき圧力は常圧のままとし、加
熱温度を90℃,130℃,160℃とした。各温度に
おけるガス状成分の留出率はそれぞれ25%,44%,
55%で沸点分布にほぼ添ったものあった。これらのガ
ス状成分をそのまま実施例4で使用したのと同じ吸着剤
を用いて実施例1と同様に処理したところ、留出液、留
出ガス共に水銀留出は全くなく、100%除去されてい
た。Example 5 Natural gas condensate containing almost no mercury (initial boiling point: 35 ° C., 50% distillation temperature: 134.5)
C., final boiling point 367 ° C.), diisopropyl mercaptomercury was added to prepare a model solution having a mercury concentration of 950 ppb (μg / l). This liquid was passed through a glass column (inner diameter 4 mm) filled with a molecular sieve 3A having a diameter of 0.3 to 0.5 mm and having a length of 30 cm with a metering pump at a flow rate of 2 ml / min. At this time, the pressure was kept at normal pressure, and the heating temperatures were 90 ° C, 130 ° C, and 160 ° C. Distillation rate of gaseous components at each temperature is 25%, 44%,
At 55%, it was almost in line with the boiling point distribution. When these gaseous components were treated as they were in the same manner as in Example 1 using the same adsorbent used in Example 4, as a result, neither distillate nor distillate gas was mercury-distilled at all and 100% was removed. Was there.
【0023】[0023]
【比較例4】吸着管を用いない以外は実施例5と同じ条
件で加熱処理試験を行い、90℃,130℃,160℃
の各温度において流出したガス状成分を冷却して液化
し、水銀を分析したところ、それぞれ90,138,2
19ppb(μg/l)であったが、その大部分は単体
水銀で、実施例5のごとく重金属硫化物を含む吸着剤に
より吸着・除去されるものであった。[Comparative Example 4] A heat treatment test was conducted under the same conditions as in Example 5 except that an adsorption tube was not used, and the temperature was 90 ° C, 130 ° C, 160 ° C.
At that temperature, the gaseous components that flowed out were cooled and liquefied, and mercury was analyzed. They were 90, 138, and 2, respectively.
It was 19 ppb (μg / l), but most of it was elemental mercury, which was adsorbed and removed by an adsorbent containing a heavy metal sulfide as in Example 5.
【0024】[0024]
【発明の効果】1.プロセスを簡略化できる。 2.設備費を低減できる。 3.後処理が不要である。 4.水銀除去と同時に重質分をカットできる。Effect of the Invention The process can be simplified. 2. Equipment costs can be reduced. 3. No post processing is required. 4. Heavy components can be cut simultaneously with mercury removal.
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 C10G 29/10 6958−4H // B01D 53/64 B01J 20/02 A 7202−4G ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI Technical indication C10G 29/10 6958-4H // B01D 53/64 B01J 20/02 A 7202-4G
Claims (3)
上の温度で加熱処理して蒸発させ、得られるガス状成分
をガス状のまま重金属硫化物を含む吸着剤に接触させる
ことを特徴とする液状炭化水素中の水銀除去法。1. A liquid hydrocarbon containing mercury is heat-treated at a temperature of 90 ° C. or higher to be evaporated, and the obtained gaseous component is brought into contact with an adsorbent containing a heavy metal sulfide in a gaseous state. Method for removing mercury in liquid hydrocarbons.
るものである請求項1記載の液状炭化水素中の水銀除去
法。2. The method for removing mercury in liquid hydrocarbons according to claim 1, wherein the adsorbent is mainly composed of molybdenum sulfide.
がMo−Co系硫化物、Mo−Ni系硫化物又はMo−
Ni−Co系硫化物を担体に担持したものである請求項
2記載の液状炭化水素中の水銀除去法。3. The molybdenum sulfide-based adsorbent is a Mo—Co based sulfide, a Mo—Ni based sulfide, or a Mo—
The method for removing mercury from liquid hydrocarbons according to claim 2, wherein the Ni-Co sulfide is supported on a carrier.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP3110709A JPH0747750B2 (en) | 1990-04-27 | 1991-04-17 | Method for removing mercury in liquid hydrocarbons |
Applications Claiming Priority (3)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2-110268 | 1990-04-27 | ||
| JP11026890 | 1990-04-27 | ||
| JP3110709A JPH0747750B2 (en) | 1990-04-27 | 1991-04-17 | Method for removing mercury in liquid hydrocarbons |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH04227794A JPH04227794A (en) | 1992-08-17 |
| JPH0747750B2 true JPH0747750B2 (en) | 1995-05-24 |
Family
ID=26449938
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP3110709A Expired - Lifetime JPH0747750B2 (en) | 1990-04-27 | 1991-04-17 | Method for removing mercury in liquid hydrocarbons |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0747750B2 (en) |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH07116446B2 (en) * | 1992-03-23 | 1995-12-13 | 日揮株式会社 | Method for removing mercury in liquid hydrocarbons |
| FR2698372B1 (en) * | 1992-11-24 | 1995-03-10 | Inst Francais Du Petrole | Process for the removal of mercury and possibly arsenic from hydrocarbons. |
| JP3847754B2 (en) | 2004-02-03 | 2006-11-22 | 石油資源開発株式会社 | Mercury removal method using distillation tower |
-
1991
- 1991-04-17 JP JP3110709A patent/JPH0747750B2/en not_active Expired - Lifetime
Also Published As
| Publication number | Publication date |
|---|---|
| JPH04227794A (en) | 1992-08-17 |
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