CA2171342A1 - Method and apparatus for absorbing hydrogen sulphide - Google Patents
Method and apparatus for absorbing hydrogen sulphideInfo
- Publication number
- CA2171342A1 CA2171342A1 CA002171342A CA2171342A CA2171342A1 CA 2171342 A1 CA2171342 A1 CA 2171342A1 CA 002171342 A CA002171342 A CA 002171342A CA 2171342 A CA2171342 A CA 2171342A CA 2171342 A1 CA2171342 A1 CA 2171342A1
- Authority
- CA
- Canada
- Prior art keywords
- gas
- solution
- hydrogen
- sulphide
- hydrogen sulphide
- 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.)
- Abandoned
Links
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 title claims abstract description 140
- 238000000034 method Methods 0.000 title claims abstract description 51
- 239000000243 solution Substances 0.000 claims abstract description 137
- 239000007789 gas Substances 0.000 claims abstract description 113
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 claims abstract description 90
- 238000010521 absorption reaction Methods 0.000 claims abstract description 89
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 claims abstract description 88
- 229910002092 carbon dioxide Inorganic materials 0.000 claims abstract description 44
- 239000001569 carbon dioxide Substances 0.000 claims abstract description 43
- 239000004291 sulphur dioxide Substances 0.000 claims abstract description 38
- 235000010269 sulphur dioxide Nutrition 0.000 claims abstract description 38
- BVKZGUZCCUSVTD-UHFFFAOYSA-L Carbonate Chemical compound [O-]C([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-L 0.000 claims abstract description 35
- 238000002485 combustion reaction Methods 0.000 claims abstract description 29
- 239000007788 liquid Substances 0.000 claims abstract description 28
- XLYOFNOQVPJJNP-UHFFFAOYSA-M hydroxide Chemical compound [OH-] XLYOFNOQVPJJNP-UHFFFAOYSA-M 0.000 claims abstract description 23
- 239000012670 alkaline solution Substances 0.000 claims abstract description 7
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 claims description 38
- 229910000029 sodium carbonate Inorganic materials 0.000 claims description 17
- 239000007864 aqueous solution Substances 0.000 claims description 13
- 239000000126 substance Substances 0.000 claims description 9
- 238000007599 discharging Methods 0.000 claims description 8
- 238000012856 packing Methods 0.000 claims description 6
- 238000004064 recycling Methods 0.000 claims description 5
- 150000008044 alkali metal hydroxides Chemical class 0.000 claims description 2
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 abstract description 93
- 238000000926 separation method Methods 0.000 abstract description 18
- 239000003513 alkali Substances 0.000 abstract description 14
- 230000008569 process Effects 0.000 abstract description 11
- 230000009102 absorption Effects 0.000 description 82
- 235000011121 sodium hydroxide Nutrition 0.000 description 29
- 229940083608 sodium hydroxide Drugs 0.000 description 20
- 235000017550 sodium carbonate Nutrition 0.000 description 16
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 13
- 229910001868 water Inorganic materials 0.000 description 13
- 239000005864 Sulphur Substances 0.000 description 12
- 229940001593 sodium carbonate Drugs 0.000 description 11
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 11
- 238000006243 chemical reaction Methods 0.000 description 10
- 239000003546 flue gas Substances 0.000 description 8
- UCKMPCXJQFINFW-UHFFFAOYSA-N Sulphide Chemical compound [S-2] UCKMPCXJQFINFW-UHFFFAOYSA-N 0.000 description 7
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 6
- 238000011084 recovery Methods 0.000 description 6
- GRVFOGOEDUUMBP-UHFFFAOYSA-N sodium sulfide (anhydrous) Chemical compound [Na+].[Na+].[S-2] GRVFOGOEDUUMBP-UHFFFAOYSA-N 0.000 description 6
- 229910021653 sulphate ion Inorganic materials 0.000 description 6
- BVKZGUZCCUSVTD-UHFFFAOYSA-M Bicarbonate Chemical compound OC([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-M 0.000 description 5
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 5
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 5
- WMFOQBRAJBCJND-UHFFFAOYSA-M Lithium hydroxide Chemical compound [Li+].[OH-] WMFOQBRAJBCJND-UHFFFAOYSA-M 0.000 description 5
- 235000011941 Tilia x europaea Nutrition 0.000 description 5
- 238000001704 evaporation Methods 0.000 description 5
- 230000008020 evaporation Effects 0.000 description 5
- 239000004571 lime Substances 0.000 description 5
- 239000010802 sludge Substances 0.000 description 5
- 229910052979 sodium sulfide Inorganic materials 0.000 description 5
- KWYUFKZDYYNOTN-UHFFFAOYSA-M Potassium hydroxide Chemical compound [OH-].[K+] KWYUFKZDYYNOTN-UHFFFAOYSA-M 0.000 description 4
- 239000001257 hydrogen Substances 0.000 description 4
- 229910052739 hydrogen Inorganic materials 0.000 description 4
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 4
- BWHMMNNQKKPAPP-UHFFFAOYSA-L potassium carbonate Chemical compound [K+].[K+].[O-]C([O-])=O BWHMMNNQKKPAPP-UHFFFAOYSA-L 0.000 description 4
- 230000001172 regenerating effect Effects 0.000 description 4
- HZAXFHJVJLSVMW-UHFFFAOYSA-N 2-Aminoethan-1-ol Chemical compound NCCO HZAXFHJVJLSVMW-UHFFFAOYSA-N 0.000 description 3
- -1 NaOH Chemical class 0.000 description 3
- PMZURENOXWZQFD-UHFFFAOYSA-L Sodium Sulfate Chemical compound [Na+].[Na+].[O-]S([O-])(=O)=O PMZURENOXWZQFD-UHFFFAOYSA-L 0.000 description 3
- 229910052783 alkali metal Inorganic materials 0.000 description 3
- 150000001340 alkali metals Chemical class 0.000 description 3
- 230000015572 biosynthetic process Effects 0.000 description 3
- 230000007423 decrease Effects 0.000 description 3
- VTHJTEIRLNZDEV-UHFFFAOYSA-L magnesium dihydroxide Chemical compound [OH-].[OH-].[Mg+2] VTHJTEIRLNZDEV-UHFFFAOYSA-L 0.000 description 3
- 239000000347 magnesium hydroxide Substances 0.000 description 3
- 229910001862 magnesium hydroxide Inorganic materials 0.000 description 3
- 235000012254 magnesium hydroxide Nutrition 0.000 description 3
- 229910052751 metal Inorganic materials 0.000 description 3
- 239000002184 metal Substances 0.000 description 3
- GEHJYWRUCIMESM-UHFFFAOYSA-L sodium sulfite Chemical compound [Na+].[Na+].[O-]S([O-])=O GEHJYWRUCIMESM-UHFFFAOYSA-L 0.000 description 3
- VTYYLEPIZMXCLO-UHFFFAOYSA-L Calcium carbonate Chemical compound [Ca+2].[O-]C([O-])=O VTYYLEPIZMXCLO-UHFFFAOYSA-L 0.000 description 2
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 2
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 2
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 description 2
- DWAQJAXMDSEUJJ-UHFFFAOYSA-M Sodium bisulfite Chemical compound [Na+].OS([O-])=O DWAQJAXMDSEUJJ-UHFFFAOYSA-M 0.000 description 2
- 230000002411 adverse Effects 0.000 description 2
- 229910000288 alkali metal carbonate Inorganic materials 0.000 description 2
- 150000008041 alkali metal carbonates Chemical class 0.000 description 2
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 2
- 229910052799 carbon Inorganic materials 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 239000000446 fuel Substances 0.000 description 2
- 150000002431 hydrogen Chemical class 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 239000000155 melt Substances 0.000 description 2
- 229910000027 potassium carbonate Inorganic materials 0.000 description 2
- 239000011734 sodium Substances 0.000 description 2
- 229910052708 sodium Inorganic materials 0.000 description 2
- 235000010267 sodium hydrogen sulphite Nutrition 0.000 description 2
- 229910052938 sodium sulfate Inorganic materials 0.000 description 2
- 235000011152 sodium sulphate Nutrition 0.000 description 2
- 235000010265 sodium sulphite Nutrition 0.000 description 2
- 239000007921 spray Substances 0.000 description 2
- JHWIEAWILPSRMU-UHFFFAOYSA-N 2-methyl-3-pyrimidin-4-ylpropanoic acid Chemical compound OC(=O)C(C)CC1=CC=NC=N1 JHWIEAWILPSRMU-UHFFFAOYSA-N 0.000 description 1
- 101100367123 Caenorhabditis elegans sul-1 gene Proteins 0.000 description 1
- 239000007832 Na2SO4 Substances 0.000 description 1
- 241000183024 Populus tremula Species 0.000 description 1
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 description 1
- 229910052784 alkaline earth metal Inorganic materials 0.000 description 1
- 150000001342 alkaline earth metals Chemical class 0.000 description 1
- 238000010420 art technique Methods 0.000 description 1
- 230000003190 augmentative effect Effects 0.000 description 1
- 229910000019 calcium carbonate Inorganic materials 0.000 description 1
- 229960003563 calcium carbonate Drugs 0.000 description 1
- 235000010216 calcium carbonate Nutrition 0.000 description 1
- 239000000920 calcium hydroxide Substances 0.000 description 1
- 235000011116 calcium hydroxide Nutrition 0.000 description 1
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 1
- 229940095643 calcium hydroxide Drugs 0.000 description 1
- 229910002091 carbon monoxide Inorganic materials 0.000 description 1
- 150000004649 carbonic acid derivatives Chemical class 0.000 description 1
- 239000003034 coal gas Substances 0.000 description 1
- 230000000052 comparative effect Effects 0.000 description 1
- ZBCBWPMODOFKDW-UHFFFAOYSA-N diethanolamine Chemical compound OCCNCCO ZBCBWPMODOFKDW-UHFFFAOYSA-N 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- 238000004880 explosion Methods 0.000 description 1
- 239000013505 freshwater Substances 0.000 description 1
- 229940076701 hydro 35 Drugs 0.000 description 1
- 150000004679 hydroxides Chemical class 0.000 description 1
- 150000002500 ions Chemical class 0.000 description 1
- XGZVUEUWXADBQD-UHFFFAOYSA-L lithium carbonate Chemical compound [Li+].[Li+].[O-]C([O-])=O XGZVUEUWXADBQD-UHFFFAOYSA-L 0.000 description 1
- 229910052808 lithium carbonate Inorganic materials 0.000 description 1
- 229960000816 magnesium hydroxide Drugs 0.000 description 1
- 239000003345 natural gas Substances 0.000 description 1
- 239000007800 oxidant agent Substances 0.000 description 1
- 239000003208 petroleum Substances 0.000 description 1
- 239000012071 phase Substances 0.000 description 1
- 229910052700 potassium Inorganic materials 0.000 description 1
- 239000011591 potassium Substances 0.000 description 1
- 229940093932 potassium hydroxide Drugs 0.000 description 1
- 235000011118 potassium hydroxide Nutrition 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- 229920006395 saturated elastomer Polymers 0.000 description 1
- 238000004904 shortening Methods 0.000 description 1
- 239000004289 sodium hydrogen sulphite Substances 0.000 description 1
- 239000007790 solid phase Substances 0.000 description 1
- 238000001179 sorption measurement Methods 0.000 description 1
- 238000005979 thermal decomposition reaction Methods 0.000 description 1
- 239000002023 wood Substances 0.000 description 1
Classifications
-
- D—TEXTILES; PAPER
- D21—PAPER-MAKING; PRODUCTION OF CELLULOSE
- D21C—PRODUCTION OF CELLULOSE BY REMOVING NON-CELLULOSE SUBSTANCES FROM CELLULOSE-CONTAINING MATERIALS; REGENERATION OF PULPING LIQUORS; APPARATUS THEREFOR
- D21C11/00—Regeneration of pulp liquors or effluent waste waters
- D21C11/06—Treatment of pulp gases; Recovery of the heat content of the gases; Treatment of gases arising from various sources in pulp and paper mills; Regeneration of gaseous SO2, e.g. arising from liquors containing sulfur compounds
- D21C11/08—Deodorisation ; Elimination of malodorous compounds, e.g. sulfur compounds such as hydrogen sulfide or mercaptans, from gas streams
-
- 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
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/48—Sulfur compounds
- B01D53/52—Hydrogen sulfide
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B17/00—Sulfur; Compounds thereof
- C01B17/64—Thiosulfates; Dithionites; Polythionates
- C01B17/66—Dithionites or hydrosulfites (S2O42-)
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P70/00—Climate change mitigation technologies in the production process for final industrial or consumer products
- Y02P70/10—Greenhouse gas [GHG] capture, material saving, heat recovery or other energy efficient measures, e.g. motor control, characterised by manufacturing processes, e.g. for rolling metal or metal working
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Organic Chemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Analytical Chemistry (AREA)
- Health & Medical Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Inorganic Chemistry (AREA)
- Biomedical Technology (AREA)
- Treating Waste Gases (AREA)
- Gas Separation By Absorption (AREA)
Abstract
A method and an apparatus for selectively removing, by liquid absorption, hydrogen sulphide from a gas containing both hydrogen sulphide and carbon dioxide, are disclosed. In a first stage of the method, the gas (3) is in a container (1) contacted, in at least one step, with a carbonate-containing alkaline solution whose pH is adjusted during the absorption by the addition of a hydroxide, such as sodium hydroxide. In a second stage of the method, the gas is combusted in a combustion device (32) for converting the hydrogen sulphide remaining in the gas to sulphur dioxide, which then is absorbed in an alkali-containing solution, such as a sodium hydroxide solution, in a wet cleaner (36). By combining the absorption of hydrogen sulphide in a carbonate-containing solution in a first stage, and the combustion of the remaining hydrogen sulphide to sulphur dioxide and the absorption of the formed sulphur dioxide in an alkaline solution in a second stage, one may attain a total hydrogen-sulphide separation of high selectivity, high degree of separation and good process economy.
Description
2~7~ 2 METHOD AND APPARATUS FOR ABSORBING HYDROGEN
SULPHIDE
.
This invention relates to a method and an apparatus for absorb-ing hydrogen sulphide, more specifically a method and an apparatus for selectively removing, by liquid absorption, hydrogen sulphide from a gas containing both hydrogen sulphide and carbon dioxide.
It is well-known that hydrogen sulphide can be removed from hydrogen-sulphide-cont~ining gases by being absorbed in an ~lk~line aqueous solution (i.e. an aqueous solution having a pH > 7), such as sodium hydroxide, or by using ethanolamine, such as monoethanol-amine and diethanolamine. Absorption may, for instance, be used for producing hydrogen sulphide in pure form, which optionally is further processed to sulphur in a Claus process. If the gas contains carbon dioxide in addition to hydrogen sulphide, the carbon dioxide will also be absorbed in the ~lk~line solution. Carbon dioxide has approximate-ly the sarne solubility in water as hydrogen sulphide, and the carbon dioxide will therefore compete with the hydrogen sulphide for being absorbed in the solution. Hydrogen sulphide and carbon dioxide are absorbed in an ~lk~line aqueous solution of e.g. sodium hydroxide in accordance with the formulae below:
H2S + OH- ~ HS-+ H20 (1) H~S + 20H- ~ S2- + 2H20 (2) C2 + OH- ~ HC03- (3) C2 + 20H- ~ C032- + H20 (4) 25 The selectivity to hydrogen sulphide, i.e. the ratio of mole of absorbed hydrogen sulphide to mole of absorbed (hydrogen sulphide + carbon dioxide~, is directly proportional to the contents of hydrogen sulphide and carbon dioxide in the gas. Thus, the competition on the part of carbon dioxide is especially pronounced when the gas contains more 30 carbon dioxide than hydrogen sulphide, as is mostly the case. If a gas contains, say, 1% by volume of hydrogen sulphide and 10% by volume of carbon dioxide and efforts are made to absorb the hydrogen sul-phide in a sodium hydroxide solution, the selectivity to hydrogen sul-phide is but 10%, i.e. 90% of the gas absorbed consists of carbon ~713~2 phide is but 10%, i.e. 90% of the gas absorbed consists of carbon dioxide, which means that as much as 90% of the sodium hydroxide is spent in absorbing carbon dioxide.
In an effort to remedy the above inconvenience in the absorption of hydrogen sulphide from gases cont~ining both hydrogen sulphide and carbon dioxide, methods for selective absorption of hydrogen sulphide have been developed. For instance, efforts have been made to selectively absorb hydrogen sulphide in solutions of strong oxidising agents, such as potassium perm~ng~n~te, sodium dichromate or ferric salts. In other selective methods, use is made of ~lk~line solutions, such as sodium carbonate or potassium carbonate solutions, the operational conditions during the absorption being carefully adjusted. More detailed information about this prior-art technique is found in an article by C. Oloman, F.E. Murray and J.B. Risk entitled "The Selective Absorption of Hydrogen Sulphide from Stack Gas", Pulp and Paper M~g~ine of C~n~ , 5 December 1969, p. 69ff, as well as an article by E. Bendall, R.C. Aiken and F. Mandas entitled "Selective Absorption of H2S from Larger Quanti-ties of CO2 by Absorption and Reaction in Fine Sprays", AICHE Jour-nal (Vol. 29, No. 1), January 1983, p. 66ff.
By using a carbonate solution, such as a sodium carbonate solution, instead of a hydroxide solution, such as a sodium hydroxide solution, the selectivity for the absorption of hydrogen sulphide can be augmented to about 30-50%. The reactions taking place during such an absorption can generally be rendered as follows:
H2S + C032- ~ HS- + HCO3- (5) C2 + C032- + H2O ~ 2HCO3- (6) When the absorption solution is a carbonate solution, the hydrogen sulphide is absorbed almost instantaneously, whereas the carbon dioxide reacts only slowly with the carbonate ions to form hydrogen carbonate ions. Owing to the high content of hydrogen car-bonate generated when using a carbonate solution as absorption medium, there is the additional advantage of a "counterpressure"
(equilibrium pressure) to the absorption of carbon dioxide, as appears from the equilibrium formula (6) above.
Wo gs/07750 ~ 1 7 ~ ~ ~L 2 PCT/SE94/00829 A problem that arises when using a carbonate solution as absorption medium is that only a fairly low hydrogen-sulphide con-tent can be achieved in the solution, owing to the reduction of the absorption capacity caused by the formation of hydrogen carbonate 5 ions. Thus, it is extremely difficult to attain hydrogen-sulphide contents exceeding about 10 g/l. As a result, prior-art methods for selectively absorbing hydrogen sulphide by means of an absorption medium in the form of a carbonate solution have not met with much success, despite the great demand for such a method in various fields 10 where hydrogen-sulphide-cont~inin~ and carbon-dioxide-con~ining gases are generated. F`~mples of such fields of application are petro-leum refinement, coal-gas production and, in particular, the combus-tion of black liquor carried out in the sulphate pulp industry.
When recovering chemicals in the sulphate pulp industry in 15 accordance with the conventional Tomlinson process, the black liquor is combusted in a soda recovery unit, resulting in the generation of steam and the formation of a melt chiefly consisting of sodium car-bonate and sodium sulphide. The melt is then dissolved in water and causticised, so that the sodium carbonate is converted to sodium 20 hydroxide and white liquor is obtained, which may then again be used for digesting wood. For many reasons, including the risk of an explo-sion when a tube in the soda recovery unit bursts, efforts have in recent years been made to develop new processes for the combustion of black liquor, in which no melt is formed. Such processes can be 25 collectively referred to as "black-liquor evaporation", and one instance thereof is the so-called SCA-Billerud process (E. Hornstedt and J. Gomy, Paper Trade Journal 158 (1974): 16, pp 32-34). In this pro-cess, the black liquor is pyrolysed in a reactor under such tempera-ture conditions that dust, which chiefly consists of sodium carbonate 30 and carbon, and a combustible gas, which inter alia contains sulphur compounds, are formed. Another instance of black-liquor evaporation is given in Swedish PatentApplication 8605116-0, which concerns a method for thermal decomposition of black liquor with concurrent supply of oxy~e~l in an amount short of the stoichiometrically required 35 amount, at a pressure above 10 bar, and at such a temperature that no melt is formed. The evaporation results in the formation of a solid phase, which chiefly consists of sodium carbonate, and a gaseous WO 95/077S0 . , PCT/SE9 1/00829 2~713~2 phase, which chiefly consists of hydrogen sulphide, carbon monoxide, carbon dioxide, hydrogen, water vapour, and methane.
In order to be able to recover the chemicals used in black-liquor evaporation as above and produce from these chemicals white liquor 5 to be used in the manufacture of pulp, it is necessary that the hydro-gen sulphide can be removed from the generated gas. Since the gas also contains carbon dioxide, the latter will compete with the hydro-gen sulphide in the liquid absorption, and since the gas has a low content of hydrogen sulphide (about 0.5-2%) and a carbon dioxide content that is some 20 times higher (about 10-20%), conventional liquid absorption results in lln.c~ti~f~ctory recovery of hydrogen sul-phide.
There is thus a need to be able to separate, by liquid absorp-tion, the hydrogen sulphide with a high degree of separation and a 15 high degree of selectivity from gases cont~ining both hydrogen sul-phide and carbon dioxide.
According to Swedish Patent Application 9300533-8, which was filed on 18 February 1993 but has not yet been published, it has been found that absorption with a high degree of separation of hydrogen 20 sulphide and a high degree of selectivity for hydrogen sulphide can be obtained by using, as a liquid absorption medium, a carbonate-cont~ining ~lk~line solution and adjusting the pH of the solution during the absorption of hydrogen sulphide by the addition of a hydroxide, i.e. not by the addition of fresh carbonate. Thus, it is 25 possible to obtain a selectivity for hydrogen sulphide in the absorption of 60-70%, a sulphide content in the absorption solution of about 30 g/l, and a degree of separation of hydrogen sulphide of about 90-99%.
To be more precise, this is attained by a method which is of the 30 type stated by way of introduction and in which the gas is contacted in at least one step with a carbonate-cont~ining ~lk~line solution whose pH is adjusted during the absorption by the addition of a hydroxide.
The inventive method can be implemented with the aid of an 35 apparatus, which is characterised in that it comprises: a container having a gas inlet and a gas outlet and cont~ining a packing arranged in a number of successive steps; means for supplying a carbonate-WO 95/07750 ~ :~L 71 3 4 2 PCT/SE94/00829 ~ ~ i containing solution to the last step, as seen in the feed direction of thegas, each step having means for supplying the carbonate-containing solution through the step countercurrently to the gas and for recycl-ing the solution over the step; conduits arranged between the steps 5 for supplying a partial flow of the solution from one step to a preced-ing step, as seen in the feed direction of the gas; means for supplying a hydroxide to the carbonate-cont~ining solution in at least one of the steps; and an outlet conduit from the first step, as seen in the feed direction of the gas, for discharging liquid cont~inin~ hydrogen sul-1 0 phide.
By "carbonate-containing ~lk~line solution" is meant an aqueous solution cont~ining carbonate ions (CO3 2-). Preferably, this solution is an alkali metal carbonate solution, such as a solution of sodium carbonate, potassium carbonate or lithium carbonate. Sodium 15 carbonate is especially preferred, being easily accessible as well as fairly inexpensive. The carbonate concentration of the solution is not critical, but conveniently is about 0.1-3 M with respect to carbonate, preferably about 1-2.5 M, and most preferred about 1.7 M.
It is essential that the carbonate-cont~ining ~lk~line solution 20 has a pH of at least about 9. pH values below about 9 result in unsa-tisfactory absorption of hydrogen sulphide, and there is even a risk that hydrogen sulphide already absorbed be released from the solu-tion. However, the pH of the solution should not be too high, since this would have an adverse effect on the absorption of hydrogen sul-25 phide, as compared with that of carbon dioxide. Thus, the pH of thesolution should preferably not exceed about 12 in order that the absorption of carbon dioxide should not be too considerable. Prefer-ably, the pH of the solution is in the range of about 10.0-11.0, and most preferred in the range of about 10.2-10.8. If the pH of the solu-30 tion is adjusted within this last narrow range, optimum separation ofhydrogen sulphide is obtained.
As appears from the equilibrium reactions (5) and (6), hydrogen carbonate ions (HCO3-) are formed in the absorption of hydrogen sul-phide and carbon dioxide. This means that the pH of the absorption 35 solution decreases as the absorption of hydrogen sulphide and carbon dioxide proceeds. When the pH of the solution goes below about 9, the absorption of hydrogen sulphide becomes unsatisfactory, as indicated WO 95107750 ~ ~ PCT/SE94100829 in the foregoing, and there is instead a risk that hydrogen sulphide already absorbed be released from the solution. If this is to be avoid-ed, the solution has to be regenerated, i.e. its pH be increased to above the lower permissible limit for a state of equilibrium between gaseous H2S and sulphide content of the liquid at the temperature and pH value at issue. However, the pH value must not be increased to above about 12, in which case the absorption of carbon dioxide would become predomin~nt. As a result of the increase of the pH of the solution brought about by the addition of a hydroxide, such as an alkali metal hydroxide, e.g. NaOH, the hydrogen carbonate ions form-ed are reconverted to carbonate ions according to the following equi-librium reaction:
OH- + HCO3- _ C032- + H2O (7) Being thus regenerated, the carbonate solution can absorb more hydrogen sulphide according to the reaction (5) above. Since the pH of the solution is adjusted by the addition of a hydroxide and maintained within the given range of about 9-12, preferably about 10.0-11.0, and most preferred about 10.2-10.8, the absorption of carbon dioxide is kept on a comparatively low level.
As indicated in the foregoing, the carbonate-containing Alk~line solution is regenerated by the addition of a hydroxide. Basically, use can be made of any hydroxide that does not have an adverse effect on the absorption of hydrogen sulphide and is capable of increasing the pH of the solution from the given lower limit of about 9 to the desired value, such as a value not exceeding about 12.0, preferably not exceeding about 11.0, and most preferred not exceeding about 10.8.
According to the invention, use is preferably made of hydroxides of alkali metals or AlkAline-earth metals, such as sodium hydroxide (NaOH), potassium hydroxide (KOH), lithium hydroxide (LiOH), cal-cium hydroxide (Ca(OH)2), and magnesium hydroxide (Mg(OH)2). For reasons of availability and cost, sodium hydroxide is most preferred.
The temperature of the liquid used in the absorption is not par-ticularly critical and may vary within a wide range, but preferably is below about 80C, since there is a risk that the absorption of hydro-gen sulphide decreases at temperatures of about 80C and above. It WO 95/07750 ~ 1713 ~ 2 PCT/SE94/00829 .
is preferred that the temperature is in the range of from room tem-perature, i.e. about 20C, to about 80C, more preferably about 40-70C, and most preferred about 60-70C.
In order to optimise the selectivity to hydrogen sulphide in the 5 liquid absorption, the absorption should be carried out in such a mamler that the flow of gas and the flow of absorbing liquid are coun-tercurrent, and the flow of gas should be turbulent and the flow of liquid laminar. Moreover, the separation of hydrogen sulphide is pro-moted if the volume of absorbing liquid is large compared with the 10 volume of gas from which hydrogen sulphide is absorbed. Such a high ratio of liquid to gas is achieved by recycling the absorbing liquid that is contacted with the hydrogen-sulphide-containing gas.
Furthermore, the contact between the sulphur-contAining gas and the absorbing liquid (the carbonate-contAining solution) may 15 involve one or more steps, preferably two or three steps, and most preferred three steps. Such multistep contact has the advantage of shortening the length of each individual step, such that the pH of the carbonate-contAining solution does not have time to fall below about 9 in the individual step, while at the same time the sulphide content 20 can be kept low in the uppermost step. Preferably, each step has such an extent or length that the pH of the solution at the end of the step has fallen to about 10.0-10.2, the liquid being then drawn offto be regenerated by means of a hydroxide and then recycled to the step at issue.
According to the invention, it has been found that the removal of hydrogen sulphide in a method of the above type can be rendered more efficient, while drastically reducing the chemical consumption, if the method is divided into two stages, namely a first stage, in which the main part of the hydrogen sulphide is removed in accordance with 30 the method described above, and a second stage, in which the remAinin~ hydrogen sulphide is essentially removed by combustion to sulphur dioxide, which is absorbed in an AlkAline solution in a wet - cleaner (scrubber). The reason for this is as follows.
As hydrogen sulphide is absorbed in the different steps of the 35 first stage, the hydrogen-sulphide content of the gas decreases, which results in a reduction of the previously-defined selectivity to hydrogen sulphide. When the selectivity is reduced, the consumption of alkali WO 95/07750 2~ 4 ~ PCT/SE94/00829 '~
increases dramatically in accordance with the reactions (5), (6) and (7) indicated above. As appears from these reactions, 1 mole of OH- is spent per mole of hydrogen sulphide absorbed, and 2 mole of OH- is spent per mole of carbon dioxide absorbed. When the selectivity to hydrogen sulphide is reduced and the absorption of carbon dioxide increases, as is the case in the last absorption step or steps of the first stage, the consumption of alkali (OH-) increases considerably.
This means that it takes a comparatively larger amount of alkali to absorb the "last" hydrogen sulphide of the gas than to absorb the "first" hydrogen sulphide of the gas. By refraining from carrying the absorption of hydrogen sulphide to the full in the first stage, but purposely leaving a certain amount of hydrogen sulphide in the gas discharged from the first stage, one avoids that the selectivity to hydrogen sulphide is dramatically reduced and, consequently, that the consumption of alkali increases dramatically in the first stage.
The hydrogen-sulphide absorption in the first stage is so carried out that the main part of the hydrogen sulphide, i.e. at least 50%, is removed. Conveniently, about 60-97%, preferably about 80-95%, and most preferred about 90%, of the hydrogen sulphide is removed in the first stage. This results in a low consumption of alkali in the first stage, which involves good process economy.
Before the gas from the first stage can be let out into the sur-rounding atmosphere, the rem~ining hydrogen sulphide must, how-ever, be removed. According to the invention, this takes place by combusting the hydrogen-sulphide-cont~ining gas from the first stage, such that the hydrogen sulphide is oxidised to sulphur dioxide, whereupon the sulphur dioxide formed is absorbed in an aqueous solution, whose pH is adjusted by the addition of an ~lk~line solution or an ~lk~line substance, in a wet cleaner (scrubber).
The present invention thus provides a method for selectively removing, by liquid adsorption, hydrogen sulphide from a gas con-t~ining both hydrogen sulphide and carbon dioxide, characterised in that the gas, in a first stage for removing the main part of the hydro-gen-sulphide content of the gas, is contacted in at least one step with a carbonate-containing ~lk~line solution whose pH is adjusted during the absorption by the addition of a hydroxide, and that the gas is then in a second stage combusted in order to convert the rem~ining hydro-W095/07750 ~ ~ 713 4 ~ PCT/SE94/00829 gen sulphide to sulphur dioxide, which is absorbed in an alkali-con-taining solution.
The invention further provides an apparatus for selectively removing, by liquid absorption, hydrogen sulphide from a gas con-5 taining both hydrogen sulphide and carbon dioxide, characterisedin that it comprises a) a container having a gas inlet and a gas outlet and containing a packing arranged in a number of successive steps; means for sup-plying a carbonate-contAining solution to the last step, as seen in the 10 feed direction of the gas, each step having means for supplying the carbonate-cont~ining solution through the step countercurrently to the gas and for recycling the solution over the step; conduits arranged between the steps for supplying a partial flow of the solution from one step to a preceding step, as seen in the feed direction of the gas;
15 means for supplying a hydroxide to the carbonate-cont~ining solution in at least one of the steps; and an outlet conduit from the first step, as seen in the feed direction of the gas, for discharging liquid con-taining hydrogen sulphide, b) a combustion device having an inlet for hydrogen-sulphide-20 contAining gas from the gas outlet of the container; combustionmeans for combusting the gas supplied and converting the hydrogen sulphide therein to sulphur dioxide; and an outlet for discharging sulphur-dioxide-cont~ining gas from the combustion device, and c) a wet cleaner adapted to absorb the sulphur dioxide formed 25 upon combustion, and comprising a container which has an inlet for sulphur-dioxide-containing gas from the combustion device; an outlet for cleaned gas; means for supplying, circ~]lAting and finely dividing an aqueous solution, whose pH is adjusted by the addition of Alk~line solution or ~lk~line substance, so as to contact it with the sulphur-30 dioxide-contAining gas supplied; and means for discharging the solu-tion that has absorbed sulphur dioxide.
Further distinctive features of the invention appear from the following description and are stated in the appended cl~3im~.
As indicated in the foregoing, the carbonate-containing ~lkAline 35 solution used in the first stage for hydrogen-sulphide absorption is an aqueous solution contAining carbonate ions, such as a solution of alkali metal carbonate, preferably sodium carbonate. When the inven-WO 95/07750 2 ~ i3 4 2 PCT/SE94/00829 10tive method is used for removing hydrogen sulphide in the sulphate pulp industry, for instance when combusting black liquor, one has found that green liquor may be used as the carbonate-containing ~lk~line solution according to the invention, and this constitutes a 5 particular aspect of the invention. Green liquor is an aqueous solution that usually contains about 1.3-1.4 mole of Na2CO3 per litre, about 0.4-0.6 mole of Na2S per litre, and about 0.3-0.5 mole of NaOH per litre. According to the invention, it has also been found that white liquor may likewise be used in the first stage as the hydroxide for 10 regenerating the carbonate-containing ~lk~line solution, when the invention is employed in the sulphate pulp industry for removing hydrogen sulphide. White liquor is an aqueous solution that con-tains NaOH, Na2S and Na2CO3, usually in the proportions of about 2.3-2.6 mole of NaOH per litre, about 0.4-0.6 mole of Na2S per litre, and about 0.25-0.4 mole of Na2CO3 per litre. Also the use of white liquor as the hydroxide for regenerating the carbonate-cont~ining ~lk~line solution constitutes a particular aspect of the invention.
Instead of white liquor, use can be made of weak liquor or oxidised white liquor for regenerating the carbonate-cont~ining 20 ~lk~line solution. By weak liquor is meant an aqueous solution that contains NaOH, Na2S and Na2CO3, usually in the proportions of about 0.3-0.4 mole of NaOH per litre, about 0.05-0.08 mole of Na2S
per litre, and about 0.05-0.07 mole of Na2CO3 per litre.
Since green liquor, white liquor as well as weak liquor contain 25 both carbonate and hydroxide, they may be used either separately or together, both as the carbonate-containing solution and for regenerat-ing the carbonate-cont~ining ~lk~line solution.
In the second stage, the combustion of the hydrogen-sulphide-cont~ining gas takes place in known m~nner in a combustion device 30 of k~own type, such as a lime sludge reburning kiln or a bark burning boiler when the invention is used in the sulphate pulp industry. If the heat content of the hydrogen-sulphide-containing gas is too low, an auxiliary fuel, such as oil or natural gas, may be used in the com-bustion to produce s~ti~f~ctory oxi-l~tion of the hydrogen sulphide to 35 sulphur dioxide. When the hydrogen-sulphide-containing gas is burnt, the hydrogen sulphide is, at normal combustion temperatures, ~ wo 95/07750 21 7~ 3 ~ 2 PCT/SE94/00829 completely oxidised to sulphur dioxide, and the gas thus contains only negligible amounts of hydrogen sulphide after the combustion.
After the combustion of the hydrogen-sulphide-containing gas in the second stage, the sulphur dioxide formed should be removed, 5 which according to the invention takes place by it being absorbed in an alkali-containing solution in a wet cleaner (scrubber). To selectively remove, by absorption in an alkali-containing solution in a scrubber, sulphur dioxide from a gas which in addition contains carbon dioxide, is a well-known technique, which need not be described in more detail 10 here. Conveniently, use is made of a scrubber where the absorbing alkali-cont~ining solution is recycled to a high extent. The pH of the alkali-containing solution in the SO2 scrubber is preferably in the range of about 6-8, and most preferred in the range of about 7-7.5. At these fairly low pH values, the absorption of carbon dioxide is neglig-15 ible, and the selectivity to the sulphur-dioxide separation consequent-ly is 100%. During the absorption, the sulphur dioxide undergoes one of the following reactions:
S2 + OH- ~ HSO3- (8) S2 + S082- + H2O ~ 2HSO3-HSO3- + OH- ~ H2O + S032- (10) As appears from the reaction formulae (8)-(10), 2 mole of OH- is spent per moie of SO2 absorbed. Since no carbon dioxide is absorbed, the absorption of sulphur dioxide can be carried out to almost 100%
of the sulphur dioxide present without there being any noticeable increase in the alkali consumption. This considerably improves pro-cess economy, as compared with the case when all the sulphur is absorbed as hydrogen sulphide in the first stage, which results in poor selectivity.
The alkali in the alkali-containing solution conveniently is a hydroxide or a carbonate of an alkali metal or an ~lk~line-earth metal, such as sodium hydroxide, potassium hydroxide, calcium carbonate, calcium hydroxide or magnesium hydroxide. Sodium hydroxide is pre-ferred, especially if the sulphur is to be recycled directly in the pro-WO 95/077~iO PCT/SE94/00829 ~7 ~
cess, e.g. when the method is employed in the sulphate pulp industry.
If so, use is conveniently made of a sodium-hydroxide-based spray scrubber, for instance of the type used by ABB Flakt Industri AB and designated the MoDo scrubber. The scrubber may then comprise one 5 or more heat-recovery steps, in which cold water is sprayed towards the hot gas, so that hot water having a temperature of about 45-65C
is obtained. After the absorption of sulphur dioxide, the solution leav-ing the scrubber contains sodium sulphite (Na2SO3), sodium hydro-gen sulphite (NaHSO3) and sodium sulphate (Na2SO4). In the sul-10 phate pulp industry, this solution can be mixed with other combust-ible process liquids, e.g. the black liquor in a pulp mill. A combustion under reducing conditions results in sulphur in the form of hydrogen sulphide, and a combustion under oxidising conditions results in sul-phur in the form sulphur dioxide.
In the pulp industry, the method according to the invention is conveniently so designed that its different stages are integrated in the existing equipment. This means that the combustion of the hydrogen-sulphide-containing gas takes place in an existing bark burning boiler or lime sludge reburning kiln. This reduces the need for other fuels in these process steps. The sulphur-dioxide-cont~ining flue gases from the bark burning boiler or the lime sludge reburning kiln can then be conducted to an existing SO2 scrubber. In this case, the only new equipment needed is a scrubber for the separation of hydrogen sul-phide.
Pulp mills may be equipped with separate SO2 scrubbers for flue gases from the bark burning boiler and the lime sludge reburning kiln and from the soda recovery boiler, respectively. When the hydro-gen-sulphide-cont~ining gas is combusted elsewhere, for example in a separate boiler, the sulphur-dioxide-cont~ining flue gases can be con-ducted to the existing SO2 scrubber for the flue gases from the soda recovery boiler.
It is evident from the foregoing that the present invention enables good process economy, a closed chemical system in which all the sulphur is recycled, as well as very low emi~sions to the sur-rounding atmosphere.
For clarifying purposes, the invention will now be described in more detail with reference to the accompanying drawings, in which ~17134~
Fi~ 1 shows a preferred apparatus according to the invention for implementing the first stage of the method according to the inven-tion; and Fig. 2 is a schematic flow chart illustrating the method accord-ing to the invention.
The apparatus shown in Fig. 1 comprises a tower or container 1 having an inlet 2 for a gas 3 which contains hydrogen sulphide as well as carbon dioxide. At the opposite end of the apparatus, there is pro-vided an outlet 4 for gas 5 from which hydrogen sulphide has been removed by liquid absorption. The contact between the hydrogen-sul-phide-containing gas and the carbonate-cont~ining solution involves three steps 6, 7 and 8. Each step contains a p~king 9, as hinted at in step 6 in the Figure. In order to optimise the selectivity to hydrogen sulphide in the absorption, the packing 9 has such a shape as to generate a l~min~r flow of liquid through the steps 6, 7 and 8. It has been found that a p~cking in the form of corrugated plates is espe cially suitable for this purpose. The packing may, for instance, be made of plastic or metal.
The contact between the hydrogen-sulphide-absorbing, carbo-nate-containing solution and the hydrogen-sulphide-containing gas is carried out in countercurrent fashion. To this end, each step has means for supplying the carbonate-cont~ining solution through the step countercurrently to the gas, as well as for recycling the solution over the step. As shown in Fig. 1, these means are made up of pumps 10, 11 and 12 which, via conduits 13, 14 and 15, feed the carbonate-cont~ining ~lk~line solution to the respective steps 6, 7 and 8, as well as conduits 16, 17 and 18 which conduct the solution from the respective steps to collecting vessels 19, 20 and 21. From these col-lecting vessels, the solution is recycled over the steps through con-duits 22, 23 and 24, which are connected to the pumps 10, 11 and 12, respectively. Fresh carbonate solution, preferably sodium carbo-nate solution, is fed to the last step 6, as seen in the feed direction of the gas, through a conduit 25 from a supply (not shown) of sodium carbonate solution.
Instead of supplying fresh carbonate solution to the last step, the carbonate solution can be generated in the last step by supplying sodiurn hydroxide solution to this step and allowing the hydroxide WO 95/07750 PCT/SE94/00829 ~
2~7:~3~
solution to absorb carbon dioxide from the gas, such that a carbo-nate-cont~ining solution is obtained according to the reactions (3)-(4) above.
In order to adjust (increase) the pH of the absorption solution, 5 a hydroxide, preferably a sodium hydroxide solution, may be supplied to the collecting vessels 19, 20 and 21 through conduits 26, 27 and 28, respectively, conducting alkali from a supply (not shown), which preferably is common to all the conduits. The supply of sodium hydroxide solution for adjusting the pH of the absorption solution is 10 regulated on the basis of the measured pH values of the solutions in the collecting vessels 19, 20 and 21 (not shown).
As appears from Fig. 1, the different steps are further inter-connected by conduits 29 and 30 for feeding a partial flow of the absorption solution from one step to the preceding step, i.e. from 15 the step 6 to the step 7 as well as from the step 7 to the step 8.
Finally, an outlet conduit 31 is arranged for discharging hydro-gen-sulphide-cont~ining liquid from the collecting vessel 21 and the step 8.
Fig. 2 is a schematic flow chart illustrating the method accord-20 ing to the invention. As indicated in the flow chart, a hydrogen-sul-phide-cont~ining and carbon-dioxide-containing gas 3 is, in a first stage, treated in an apparatus which includes a container 1 for the absorption of hydrogen sulphide, as described in the foregoing with reference to Fig. 1. According to the invention, the absorption of 25 hydrogen sulphide is not, in the first stage, carried out to 100%, i.e.
total absorption of hydrogen sulphide in the first stage, but only so far that at least the main part of the hydrogen sulphide, i.e. at least 50%, preferably about 60-97%, more preferably about 80-95% and most preferred about 90%, of the hydrogen sulphide is absorbed in the first 30 stage. Preferably, a total of at least about 98% of the hydrogen-sul-phide content of the gas is absorbed by the first and the second stage.
The thus-cleaned gas 5, which still contains hydrogen sulphide and carbon dioxide, is then fed from the first stage to the second stage, in which the gas is first combusted in order to convert hydro-35 gen sulphide to sulphur dioxide, and then wet-cleaned in a scrubber in view of the absorption of the sulphur dioxide formed.
~ WO 95/07750 PCTISE94/00829 I ~17~3~2 As indicated in Fig. 2, the combustion takes place in a combus-tion device 32, which has combustion means 33, e.g. a burner, for combusting the gas 5 supplied through an inlet 34 and oxidising the hydrogen sulphide to sulphur dioxide. As mentioned in the foregoing, the combustion device 32 may consist of existing equipment, such as a bark burning boiler or a lime sludge reburning kiln. The sulphur-dioxide-containing flue gas is discharged through an outlet 35 and conducted to a wet cleaner 36, which comprises a container 37 having an inlet 38 for the sulphur-dioxide-containing gas, an outlet 39 for the cleaned gas 40, and means 41 for supplying an alkali-cont~ining solution. As mentioned above, the alkali-containing solution contains a hydroxide of an alkali metal or ~lk~line-earth metal, preferably sodium hydroxide. The solution is circulated by means of a pump 42 to nozzles 43, where it is finely divided and is countercurrently brought into contact with the sulphur-dioxide-cont~ining gas, such that the sulphur dioxide is absorbed by the solution. In order to opti-mise the absorption of sulphur dioxide, without any competing absorption of carbon dioxide, the pH of the solution is adjusted to about 6-8, preferably 7-7.5. The solution that has absorbed sulphur dio~ide is discharged from the second stage at 44.
The invention will now be further elucidated with the aid of a non-restricting Example.
F~x~rnple A test was performed for the selective removal of hydrogen sul-phide from a gas generated in black-liquor evaporation. Use was made of an apparatus of the type described above and shown in Figs 1 and 2.
In the first stage of the method, the absorption of hydrogen sul-phide took place at atmospheric pressure, and the feed gas had a temperature of about 60C and contained 1.13 mole % of hydrogen - sulphide and 16.9 mole % of carbon dioxide. The gas was saturated with water vapour at the temperature at issue, which corresponded to about 18.7 mole % of water. The feed gas flow was 38280 Nm3/h, giving the gas a velocity of about 3.1 m/ s in the absorption tower. The absorption tower had a height of 6.25 m, and the two first steps each had a height of 1.5 m, whereas the last step, as seen in the feed direction of the gas, had a height of 1 m. Each step was provided with WO 95/07750 2 ~ 71`~ 4 ~ PCT/SE94/00829 a packing of the type Mellapack 500 from Sulzer. The diameter of the tower was 2.3 m.
Fresh absorption solution, which consisted of 8.8 m3/h of 2 M
sodium carbonate solution having a temperature of about 60C, was supplied to the last step in the tower along with recycled absorption solution, such that a total of about 50 m3/h of absorption solution was supplied to the last step in the tower. The pH of the absorption solution supplied was about 11.0, which was reduced to about 10.2 during the passage of the solution through the step owing to the 10 absorption of hydrogen sulphide. After passing through the step, the solution was supplied to a 1.5 m3 collecting vessel, where the solution was regenerated by the addition of a 2.5 M sodium hydroxide solution having a temperature of about 60C, such that the pH of the solution was again increased to about 11Ø Then, the regenerated solution 15 was recycled by means of a pump to the last step in the absorption tower for renewed absorption of hydrogen sulphide.
About 11 m3/h of the absorption solution was drawn off from the collecting vessel to the collecting vessel of the intermediate step, whence about 50 m3/h of the absorption solution having a pH of 20 about 11.0 was pumped, as in the previous step, to the intermediate step, whence the absorption solution was drawn off at a pH of about 10.2 to be recycled to the collecting vessel. In the collecting vessel, the solution was regenerated by the addition of a 2.5 M sodium hydroxide solution having a temperature of about 60C, as in the previous step.
From the collecting vessel of the intermediate step, about 13.5 m3/h of the absorption solution was drawn off to the collecting vessel of the first (lowermost) step, whence 50 m3/h of the absorption solution having a pH of about 11.0 was pumped to the first step, as seen in the feed direction of the gas. After passing this step and there 30 absorbing hydrogen sulphide, the solution, now having a pH of about 10.2, was drawn off to be recycled to the collecting vessel. In the col-lecting vessel, the solution was regenerated as in the previous steps by the addition of a 2.5 M sodium hydroxide solution having a tempe-rature of about 60C, such that the pH of the regenerated solution 35 was about 11Ø All in all, about 8.6 m3/h of the 2.5 M sodium hydroxide solution was added to the collecting vessels of the three steps.
~ WO 95/07750 PCT/SE94/00829 2~7~2 From the collecting vessel of the first (lowermost) step, about 17.4 m3/h of the solution having a HS- concentration of 1 mole/l was drawn off. The gas leaving the absorption tower contained 0.113 mole % of hydrogen sulphide and 16.4 mole % of carbon dioxide. In the 5 first stage of the method, the degree of separation of hydrogen sul-phide was about 90%, and the selectivity to hydrogen sulphide in the separation was about 0.67%.
Then came the second stage of the method. Thus, the gas leav-ing the absorption tower in the first stage was combusted in a fur-nace to which was added 31700 Nm3/h of air, which resulted in 66000 Nm3/ h of flue gas cont~ining 650 ppm of SO2 (1930 mole/h).
This flue gas was conducted to an SO2 scrubber of conventional type desclibed in the foregoing. In the scrubber, 1.54 m3/h of the 2.5 M
sodium hydroxide solution was spent, and 2.0 m3/h of fresh water was in addition supplied to the scrubber in order to cool the incoming flue gas to saturation temperature. The gas leaving the scrubber had an So2 concentration of 12 ppm, which corresponded to 35 mole/h (1.12 kg/h of sulphur). The supplied absorption solution was kept at a constant pH of 7.2. The absorption solution was recycled in th scrubber at a total flow rate of 170 m3/h. From the scrubber was drawn off 1.8 m3/h of the solution, which had a total sulphur con-centration (S032- + HSO3- + S042-) of 1.05 mole/l. The total degree of separation of sulphur, i.e. the degree of separation of hydrogen sulphide in the first stage plus the degree of separation of sulphur dioxide in the second stage, thus was 99.8%. In the first stage, 860 kg/h of sodium hydroxide was spent, and in the second stage, 152 kg/h of sodium hydroxide was spent, i.e. a total of 1012 kg/h of NaOH was spent in order to obtain a degree of separation of sulphur of 99.8%.
For comparative purposes, the method was repeated, but this time only with the first stage, i.e. the combustion of hydrogen sul-phide to sulphur dioxide and the absorption of the formed sulphur dioxide in a wet scrubber were not performed. Instead, the separation of hydrogen sulphide in the first stage was carried out to such an extent that 98% of the hydrogen sulphide was separated. The selec-tivity to hydrogen sulphide in a 90-98% separation of hydrogen sul-phide is 0.15. The total selectivity for the whole stage then is about WO 95/07750 21 7 ~ 3 4 2 PCT/SE94/00829 ' . . , NaOH consumption more than 70% higher than in the inventive method, despite the fact that the total degree of separation of sulphur was lower.
SULPHIDE
.
This invention relates to a method and an apparatus for absorb-ing hydrogen sulphide, more specifically a method and an apparatus for selectively removing, by liquid absorption, hydrogen sulphide from a gas containing both hydrogen sulphide and carbon dioxide.
It is well-known that hydrogen sulphide can be removed from hydrogen-sulphide-cont~ining gases by being absorbed in an ~lk~line aqueous solution (i.e. an aqueous solution having a pH > 7), such as sodium hydroxide, or by using ethanolamine, such as monoethanol-amine and diethanolamine. Absorption may, for instance, be used for producing hydrogen sulphide in pure form, which optionally is further processed to sulphur in a Claus process. If the gas contains carbon dioxide in addition to hydrogen sulphide, the carbon dioxide will also be absorbed in the ~lk~line solution. Carbon dioxide has approximate-ly the sarne solubility in water as hydrogen sulphide, and the carbon dioxide will therefore compete with the hydrogen sulphide for being absorbed in the solution. Hydrogen sulphide and carbon dioxide are absorbed in an ~lk~line aqueous solution of e.g. sodium hydroxide in accordance with the formulae below:
H2S + OH- ~ HS-+ H20 (1) H~S + 20H- ~ S2- + 2H20 (2) C2 + OH- ~ HC03- (3) C2 + 20H- ~ C032- + H20 (4) 25 The selectivity to hydrogen sulphide, i.e. the ratio of mole of absorbed hydrogen sulphide to mole of absorbed (hydrogen sulphide + carbon dioxide~, is directly proportional to the contents of hydrogen sulphide and carbon dioxide in the gas. Thus, the competition on the part of carbon dioxide is especially pronounced when the gas contains more 30 carbon dioxide than hydrogen sulphide, as is mostly the case. If a gas contains, say, 1% by volume of hydrogen sulphide and 10% by volume of carbon dioxide and efforts are made to absorb the hydrogen sul-phide in a sodium hydroxide solution, the selectivity to hydrogen sul-phide is but 10%, i.e. 90% of the gas absorbed consists of carbon ~713~2 phide is but 10%, i.e. 90% of the gas absorbed consists of carbon dioxide, which means that as much as 90% of the sodium hydroxide is spent in absorbing carbon dioxide.
In an effort to remedy the above inconvenience in the absorption of hydrogen sulphide from gases cont~ining both hydrogen sulphide and carbon dioxide, methods for selective absorption of hydrogen sulphide have been developed. For instance, efforts have been made to selectively absorb hydrogen sulphide in solutions of strong oxidising agents, such as potassium perm~ng~n~te, sodium dichromate or ferric salts. In other selective methods, use is made of ~lk~line solutions, such as sodium carbonate or potassium carbonate solutions, the operational conditions during the absorption being carefully adjusted. More detailed information about this prior-art technique is found in an article by C. Oloman, F.E. Murray and J.B. Risk entitled "The Selective Absorption of Hydrogen Sulphide from Stack Gas", Pulp and Paper M~g~ine of C~n~ , 5 December 1969, p. 69ff, as well as an article by E. Bendall, R.C. Aiken and F. Mandas entitled "Selective Absorption of H2S from Larger Quanti-ties of CO2 by Absorption and Reaction in Fine Sprays", AICHE Jour-nal (Vol. 29, No. 1), January 1983, p. 66ff.
By using a carbonate solution, such as a sodium carbonate solution, instead of a hydroxide solution, such as a sodium hydroxide solution, the selectivity for the absorption of hydrogen sulphide can be augmented to about 30-50%. The reactions taking place during such an absorption can generally be rendered as follows:
H2S + C032- ~ HS- + HCO3- (5) C2 + C032- + H2O ~ 2HCO3- (6) When the absorption solution is a carbonate solution, the hydrogen sulphide is absorbed almost instantaneously, whereas the carbon dioxide reacts only slowly with the carbonate ions to form hydrogen carbonate ions. Owing to the high content of hydrogen car-bonate generated when using a carbonate solution as absorption medium, there is the additional advantage of a "counterpressure"
(equilibrium pressure) to the absorption of carbon dioxide, as appears from the equilibrium formula (6) above.
Wo gs/07750 ~ 1 7 ~ ~ ~L 2 PCT/SE94/00829 A problem that arises when using a carbonate solution as absorption medium is that only a fairly low hydrogen-sulphide con-tent can be achieved in the solution, owing to the reduction of the absorption capacity caused by the formation of hydrogen carbonate 5 ions. Thus, it is extremely difficult to attain hydrogen-sulphide contents exceeding about 10 g/l. As a result, prior-art methods for selectively absorbing hydrogen sulphide by means of an absorption medium in the form of a carbonate solution have not met with much success, despite the great demand for such a method in various fields 10 where hydrogen-sulphide-cont~inin~ and carbon-dioxide-con~ining gases are generated. F`~mples of such fields of application are petro-leum refinement, coal-gas production and, in particular, the combus-tion of black liquor carried out in the sulphate pulp industry.
When recovering chemicals in the sulphate pulp industry in 15 accordance with the conventional Tomlinson process, the black liquor is combusted in a soda recovery unit, resulting in the generation of steam and the formation of a melt chiefly consisting of sodium car-bonate and sodium sulphide. The melt is then dissolved in water and causticised, so that the sodium carbonate is converted to sodium 20 hydroxide and white liquor is obtained, which may then again be used for digesting wood. For many reasons, including the risk of an explo-sion when a tube in the soda recovery unit bursts, efforts have in recent years been made to develop new processes for the combustion of black liquor, in which no melt is formed. Such processes can be 25 collectively referred to as "black-liquor evaporation", and one instance thereof is the so-called SCA-Billerud process (E. Hornstedt and J. Gomy, Paper Trade Journal 158 (1974): 16, pp 32-34). In this pro-cess, the black liquor is pyrolysed in a reactor under such tempera-ture conditions that dust, which chiefly consists of sodium carbonate 30 and carbon, and a combustible gas, which inter alia contains sulphur compounds, are formed. Another instance of black-liquor evaporation is given in Swedish PatentApplication 8605116-0, which concerns a method for thermal decomposition of black liquor with concurrent supply of oxy~e~l in an amount short of the stoichiometrically required 35 amount, at a pressure above 10 bar, and at such a temperature that no melt is formed. The evaporation results in the formation of a solid phase, which chiefly consists of sodium carbonate, and a gaseous WO 95/077S0 . , PCT/SE9 1/00829 2~713~2 phase, which chiefly consists of hydrogen sulphide, carbon monoxide, carbon dioxide, hydrogen, water vapour, and methane.
In order to be able to recover the chemicals used in black-liquor evaporation as above and produce from these chemicals white liquor 5 to be used in the manufacture of pulp, it is necessary that the hydro-gen sulphide can be removed from the generated gas. Since the gas also contains carbon dioxide, the latter will compete with the hydro-gen sulphide in the liquid absorption, and since the gas has a low content of hydrogen sulphide (about 0.5-2%) and a carbon dioxide content that is some 20 times higher (about 10-20%), conventional liquid absorption results in lln.c~ti~f~ctory recovery of hydrogen sul-phide.
There is thus a need to be able to separate, by liquid absorp-tion, the hydrogen sulphide with a high degree of separation and a 15 high degree of selectivity from gases cont~ining both hydrogen sul-phide and carbon dioxide.
According to Swedish Patent Application 9300533-8, which was filed on 18 February 1993 but has not yet been published, it has been found that absorption with a high degree of separation of hydrogen 20 sulphide and a high degree of selectivity for hydrogen sulphide can be obtained by using, as a liquid absorption medium, a carbonate-cont~ining ~lk~line solution and adjusting the pH of the solution during the absorption of hydrogen sulphide by the addition of a hydroxide, i.e. not by the addition of fresh carbonate. Thus, it is 25 possible to obtain a selectivity for hydrogen sulphide in the absorption of 60-70%, a sulphide content in the absorption solution of about 30 g/l, and a degree of separation of hydrogen sulphide of about 90-99%.
To be more precise, this is attained by a method which is of the 30 type stated by way of introduction and in which the gas is contacted in at least one step with a carbonate-cont~ining ~lk~line solution whose pH is adjusted during the absorption by the addition of a hydroxide.
The inventive method can be implemented with the aid of an 35 apparatus, which is characterised in that it comprises: a container having a gas inlet and a gas outlet and cont~ining a packing arranged in a number of successive steps; means for supplying a carbonate-WO 95/07750 ~ :~L 71 3 4 2 PCT/SE94/00829 ~ ~ i containing solution to the last step, as seen in the feed direction of thegas, each step having means for supplying the carbonate-containing solution through the step countercurrently to the gas and for recycl-ing the solution over the step; conduits arranged between the steps 5 for supplying a partial flow of the solution from one step to a preced-ing step, as seen in the feed direction of the gas; means for supplying a hydroxide to the carbonate-cont~ining solution in at least one of the steps; and an outlet conduit from the first step, as seen in the feed direction of the gas, for discharging liquid cont~inin~ hydrogen sul-1 0 phide.
By "carbonate-containing ~lk~line solution" is meant an aqueous solution cont~ining carbonate ions (CO3 2-). Preferably, this solution is an alkali metal carbonate solution, such as a solution of sodium carbonate, potassium carbonate or lithium carbonate. Sodium 15 carbonate is especially preferred, being easily accessible as well as fairly inexpensive. The carbonate concentration of the solution is not critical, but conveniently is about 0.1-3 M with respect to carbonate, preferably about 1-2.5 M, and most preferred about 1.7 M.
It is essential that the carbonate-cont~ining ~lk~line solution 20 has a pH of at least about 9. pH values below about 9 result in unsa-tisfactory absorption of hydrogen sulphide, and there is even a risk that hydrogen sulphide already absorbed be released from the solu-tion. However, the pH of the solution should not be too high, since this would have an adverse effect on the absorption of hydrogen sul-25 phide, as compared with that of carbon dioxide. Thus, the pH of thesolution should preferably not exceed about 12 in order that the absorption of carbon dioxide should not be too considerable. Prefer-ably, the pH of the solution is in the range of about 10.0-11.0, and most preferred in the range of about 10.2-10.8. If the pH of the solu-30 tion is adjusted within this last narrow range, optimum separation ofhydrogen sulphide is obtained.
As appears from the equilibrium reactions (5) and (6), hydrogen carbonate ions (HCO3-) are formed in the absorption of hydrogen sul-phide and carbon dioxide. This means that the pH of the absorption 35 solution decreases as the absorption of hydrogen sulphide and carbon dioxide proceeds. When the pH of the solution goes below about 9, the absorption of hydrogen sulphide becomes unsatisfactory, as indicated WO 95107750 ~ ~ PCT/SE94100829 in the foregoing, and there is instead a risk that hydrogen sulphide already absorbed be released from the solution. If this is to be avoid-ed, the solution has to be regenerated, i.e. its pH be increased to above the lower permissible limit for a state of equilibrium between gaseous H2S and sulphide content of the liquid at the temperature and pH value at issue. However, the pH value must not be increased to above about 12, in which case the absorption of carbon dioxide would become predomin~nt. As a result of the increase of the pH of the solution brought about by the addition of a hydroxide, such as an alkali metal hydroxide, e.g. NaOH, the hydrogen carbonate ions form-ed are reconverted to carbonate ions according to the following equi-librium reaction:
OH- + HCO3- _ C032- + H2O (7) Being thus regenerated, the carbonate solution can absorb more hydrogen sulphide according to the reaction (5) above. Since the pH of the solution is adjusted by the addition of a hydroxide and maintained within the given range of about 9-12, preferably about 10.0-11.0, and most preferred about 10.2-10.8, the absorption of carbon dioxide is kept on a comparatively low level.
As indicated in the foregoing, the carbonate-containing Alk~line solution is regenerated by the addition of a hydroxide. Basically, use can be made of any hydroxide that does not have an adverse effect on the absorption of hydrogen sulphide and is capable of increasing the pH of the solution from the given lower limit of about 9 to the desired value, such as a value not exceeding about 12.0, preferably not exceeding about 11.0, and most preferred not exceeding about 10.8.
According to the invention, use is preferably made of hydroxides of alkali metals or AlkAline-earth metals, such as sodium hydroxide (NaOH), potassium hydroxide (KOH), lithium hydroxide (LiOH), cal-cium hydroxide (Ca(OH)2), and magnesium hydroxide (Mg(OH)2). For reasons of availability and cost, sodium hydroxide is most preferred.
The temperature of the liquid used in the absorption is not par-ticularly critical and may vary within a wide range, but preferably is below about 80C, since there is a risk that the absorption of hydro-gen sulphide decreases at temperatures of about 80C and above. It WO 95/07750 ~ 1713 ~ 2 PCT/SE94/00829 .
is preferred that the temperature is in the range of from room tem-perature, i.e. about 20C, to about 80C, more preferably about 40-70C, and most preferred about 60-70C.
In order to optimise the selectivity to hydrogen sulphide in the 5 liquid absorption, the absorption should be carried out in such a mamler that the flow of gas and the flow of absorbing liquid are coun-tercurrent, and the flow of gas should be turbulent and the flow of liquid laminar. Moreover, the separation of hydrogen sulphide is pro-moted if the volume of absorbing liquid is large compared with the 10 volume of gas from which hydrogen sulphide is absorbed. Such a high ratio of liquid to gas is achieved by recycling the absorbing liquid that is contacted with the hydrogen-sulphide-containing gas.
Furthermore, the contact between the sulphur-contAining gas and the absorbing liquid (the carbonate-contAining solution) may 15 involve one or more steps, preferably two or three steps, and most preferred three steps. Such multistep contact has the advantage of shortening the length of each individual step, such that the pH of the carbonate-contAining solution does not have time to fall below about 9 in the individual step, while at the same time the sulphide content 20 can be kept low in the uppermost step. Preferably, each step has such an extent or length that the pH of the solution at the end of the step has fallen to about 10.0-10.2, the liquid being then drawn offto be regenerated by means of a hydroxide and then recycled to the step at issue.
According to the invention, it has been found that the removal of hydrogen sulphide in a method of the above type can be rendered more efficient, while drastically reducing the chemical consumption, if the method is divided into two stages, namely a first stage, in which the main part of the hydrogen sulphide is removed in accordance with 30 the method described above, and a second stage, in which the remAinin~ hydrogen sulphide is essentially removed by combustion to sulphur dioxide, which is absorbed in an AlkAline solution in a wet - cleaner (scrubber). The reason for this is as follows.
As hydrogen sulphide is absorbed in the different steps of the 35 first stage, the hydrogen-sulphide content of the gas decreases, which results in a reduction of the previously-defined selectivity to hydrogen sulphide. When the selectivity is reduced, the consumption of alkali WO 95/07750 2~ 4 ~ PCT/SE94/00829 '~
increases dramatically in accordance with the reactions (5), (6) and (7) indicated above. As appears from these reactions, 1 mole of OH- is spent per mole of hydrogen sulphide absorbed, and 2 mole of OH- is spent per mole of carbon dioxide absorbed. When the selectivity to hydrogen sulphide is reduced and the absorption of carbon dioxide increases, as is the case in the last absorption step or steps of the first stage, the consumption of alkali (OH-) increases considerably.
This means that it takes a comparatively larger amount of alkali to absorb the "last" hydrogen sulphide of the gas than to absorb the "first" hydrogen sulphide of the gas. By refraining from carrying the absorption of hydrogen sulphide to the full in the first stage, but purposely leaving a certain amount of hydrogen sulphide in the gas discharged from the first stage, one avoids that the selectivity to hydrogen sulphide is dramatically reduced and, consequently, that the consumption of alkali increases dramatically in the first stage.
The hydrogen-sulphide absorption in the first stage is so carried out that the main part of the hydrogen sulphide, i.e. at least 50%, is removed. Conveniently, about 60-97%, preferably about 80-95%, and most preferred about 90%, of the hydrogen sulphide is removed in the first stage. This results in a low consumption of alkali in the first stage, which involves good process economy.
Before the gas from the first stage can be let out into the sur-rounding atmosphere, the rem~ining hydrogen sulphide must, how-ever, be removed. According to the invention, this takes place by combusting the hydrogen-sulphide-cont~ining gas from the first stage, such that the hydrogen sulphide is oxidised to sulphur dioxide, whereupon the sulphur dioxide formed is absorbed in an aqueous solution, whose pH is adjusted by the addition of an ~lk~line solution or an ~lk~line substance, in a wet cleaner (scrubber).
The present invention thus provides a method for selectively removing, by liquid adsorption, hydrogen sulphide from a gas con-t~ining both hydrogen sulphide and carbon dioxide, characterised in that the gas, in a first stage for removing the main part of the hydro-gen-sulphide content of the gas, is contacted in at least one step with a carbonate-containing ~lk~line solution whose pH is adjusted during the absorption by the addition of a hydroxide, and that the gas is then in a second stage combusted in order to convert the rem~ining hydro-W095/07750 ~ ~ 713 4 ~ PCT/SE94/00829 gen sulphide to sulphur dioxide, which is absorbed in an alkali-con-taining solution.
The invention further provides an apparatus for selectively removing, by liquid absorption, hydrogen sulphide from a gas con-5 taining both hydrogen sulphide and carbon dioxide, characterisedin that it comprises a) a container having a gas inlet and a gas outlet and containing a packing arranged in a number of successive steps; means for sup-plying a carbonate-contAining solution to the last step, as seen in the 10 feed direction of the gas, each step having means for supplying the carbonate-cont~ining solution through the step countercurrently to the gas and for recycling the solution over the step; conduits arranged between the steps for supplying a partial flow of the solution from one step to a preceding step, as seen in the feed direction of the gas;
15 means for supplying a hydroxide to the carbonate-cont~ining solution in at least one of the steps; and an outlet conduit from the first step, as seen in the feed direction of the gas, for discharging liquid con-taining hydrogen sulphide, b) a combustion device having an inlet for hydrogen-sulphide-20 contAining gas from the gas outlet of the container; combustionmeans for combusting the gas supplied and converting the hydrogen sulphide therein to sulphur dioxide; and an outlet for discharging sulphur-dioxide-cont~ining gas from the combustion device, and c) a wet cleaner adapted to absorb the sulphur dioxide formed 25 upon combustion, and comprising a container which has an inlet for sulphur-dioxide-containing gas from the combustion device; an outlet for cleaned gas; means for supplying, circ~]lAting and finely dividing an aqueous solution, whose pH is adjusted by the addition of Alk~line solution or ~lk~line substance, so as to contact it with the sulphur-30 dioxide-contAining gas supplied; and means for discharging the solu-tion that has absorbed sulphur dioxide.
Further distinctive features of the invention appear from the following description and are stated in the appended cl~3im~.
As indicated in the foregoing, the carbonate-containing ~lkAline 35 solution used in the first stage for hydrogen-sulphide absorption is an aqueous solution contAining carbonate ions, such as a solution of alkali metal carbonate, preferably sodium carbonate. When the inven-WO 95/07750 2 ~ i3 4 2 PCT/SE94/00829 10tive method is used for removing hydrogen sulphide in the sulphate pulp industry, for instance when combusting black liquor, one has found that green liquor may be used as the carbonate-containing ~lk~line solution according to the invention, and this constitutes a 5 particular aspect of the invention. Green liquor is an aqueous solution that usually contains about 1.3-1.4 mole of Na2CO3 per litre, about 0.4-0.6 mole of Na2S per litre, and about 0.3-0.5 mole of NaOH per litre. According to the invention, it has also been found that white liquor may likewise be used in the first stage as the hydroxide for 10 regenerating the carbonate-containing ~lk~line solution, when the invention is employed in the sulphate pulp industry for removing hydrogen sulphide. White liquor is an aqueous solution that con-tains NaOH, Na2S and Na2CO3, usually in the proportions of about 2.3-2.6 mole of NaOH per litre, about 0.4-0.6 mole of Na2S per litre, and about 0.25-0.4 mole of Na2CO3 per litre. Also the use of white liquor as the hydroxide for regenerating the carbonate-cont~ining ~lk~line solution constitutes a particular aspect of the invention.
Instead of white liquor, use can be made of weak liquor or oxidised white liquor for regenerating the carbonate-cont~ining 20 ~lk~line solution. By weak liquor is meant an aqueous solution that contains NaOH, Na2S and Na2CO3, usually in the proportions of about 0.3-0.4 mole of NaOH per litre, about 0.05-0.08 mole of Na2S
per litre, and about 0.05-0.07 mole of Na2CO3 per litre.
Since green liquor, white liquor as well as weak liquor contain 25 both carbonate and hydroxide, they may be used either separately or together, both as the carbonate-containing solution and for regenerat-ing the carbonate-cont~ining ~lk~line solution.
In the second stage, the combustion of the hydrogen-sulphide-cont~ining gas takes place in known m~nner in a combustion device 30 of k~own type, such as a lime sludge reburning kiln or a bark burning boiler when the invention is used in the sulphate pulp industry. If the heat content of the hydrogen-sulphide-containing gas is too low, an auxiliary fuel, such as oil or natural gas, may be used in the com-bustion to produce s~ti~f~ctory oxi-l~tion of the hydrogen sulphide to 35 sulphur dioxide. When the hydrogen-sulphide-containing gas is burnt, the hydrogen sulphide is, at normal combustion temperatures, ~ wo 95/07750 21 7~ 3 ~ 2 PCT/SE94/00829 completely oxidised to sulphur dioxide, and the gas thus contains only negligible amounts of hydrogen sulphide after the combustion.
After the combustion of the hydrogen-sulphide-containing gas in the second stage, the sulphur dioxide formed should be removed, 5 which according to the invention takes place by it being absorbed in an alkali-containing solution in a wet cleaner (scrubber). To selectively remove, by absorption in an alkali-containing solution in a scrubber, sulphur dioxide from a gas which in addition contains carbon dioxide, is a well-known technique, which need not be described in more detail 10 here. Conveniently, use is made of a scrubber where the absorbing alkali-cont~ining solution is recycled to a high extent. The pH of the alkali-containing solution in the SO2 scrubber is preferably in the range of about 6-8, and most preferred in the range of about 7-7.5. At these fairly low pH values, the absorption of carbon dioxide is neglig-15 ible, and the selectivity to the sulphur-dioxide separation consequent-ly is 100%. During the absorption, the sulphur dioxide undergoes one of the following reactions:
S2 + OH- ~ HSO3- (8) S2 + S082- + H2O ~ 2HSO3-HSO3- + OH- ~ H2O + S032- (10) As appears from the reaction formulae (8)-(10), 2 mole of OH- is spent per moie of SO2 absorbed. Since no carbon dioxide is absorbed, the absorption of sulphur dioxide can be carried out to almost 100%
of the sulphur dioxide present without there being any noticeable increase in the alkali consumption. This considerably improves pro-cess economy, as compared with the case when all the sulphur is absorbed as hydrogen sulphide in the first stage, which results in poor selectivity.
The alkali in the alkali-containing solution conveniently is a hydroxide or a carbonate of an alkali metal or an ~lk~line-earth metal, such as sodium hydroxide, potassium hydroxide, calcium carbonate, calcium hydroxide or magnesium hydroxide. Sodium hydroxide is pre-ferred, especially if the sulphur is to be recycled directly in the pro-WO 95/077~iO PCT/SE94/00829 ~7 ~
cess, e.g. when the method is employed in the sulphate pulp industry.
If so, use is conveniently made of a sodium-hydroxide-based spray scrubber, for instance of the type used by ABB Flakt Industri AB and designated the MoDo scrubber. The scrubber may then comprise one 5 or more heat-recovery steps, in which cold water is sprayed towards the hot gas, so that hot water having a temperature of about 45-65C
is obtained. After the absorption of sulphur dioxide, the solution leav-ing the scrubber contains sodium sulphite (Na2SO3), sodium hydro-gen sulphite (NaHSO3) and sodium sulphate (Na2SO4). In the sul-10 phate pulp industry, this solution can be mixed with other combust-ible process liquids, e.g. the black liquor in a pulp mill. A combustion under reducing conditions results in sulphur in the form of hydrogen sulphide, and a combustion under oxidising conditions results in sul-phur in the form sulphur dioxide.
In the pulp industry, the method according to the invention is conveniently so designed that its different stages are integrated in the existing equipment. This means that the combustion of the hydrogen-sulphide-containing gas takes place in an existing bark burning boiler or lime sludge reburning kiln. This reduces the need for other fuels in these process steps. The sulphur-dioxide-cont~ining flue gases from the bark burning boiler or the lime sludge reburning kiln can then be conducted to an existing SO2 scrubber. In this case, the only new equipment needed is a scrubber for the separation of hydrogen sul-phide.
Pulp mills may be equipped with separate SO2 scrubbers for flue gases from the bark burning boiler and the lime sludge reburning kiln and from the soda recovery boiler, respectively. When the hydro-gen-sulphide-cont~ining gas is combusted elsewhere, for example in a separate boiler, the sulphur-dioxide-cont~ining flue gases can be con-ducted to the existing SO2 scrubber for the flue gases from the soda recovery boiler.
It is evident from the foregoing that the present invention enables good process economy, a closed chemical system in which all the sulphur is recycled, as well as very low emi~sions to the sur-rounding atmosphere.
For clarifying purposes, the invention will now be described in more detail with reference to the accompanying drawings, in which ~17134~
Fi~ 1 shows a preferred apparatus according to the invention for implementing the first stage of the method according to the inven-tion; and Fig. 2 is a schematic flow chart illustrating the method accord-ing to the invention.
The apparatus shown in Fig. 1 comprises a tower or container 1 having an inlet 2 for a gas 3 which contains hydrogen sulphide as well as carbon dioxide. At the opposite end of the apparatus, there is pro-vided an outlet 4 for gas 5 from which hydrogen sulphide has been removed by liquid absorption. The contact between the hydrogen-sul-phide-containing gas and the carbonate-cont~ining solution involves three steps 6, 7 and 8. Each step contains a p~king 9, as hinted at in step 6 in the Figure. In order to optimise the selectivity to hydrogen sulphide in the absorption, the packing 9 has such a shape as to generate a l~min~r flow of liquid through the steps 6, 7 and 8. It has been found that a p~cking in the form of corrugated plates is espe cially suitable for this purpose. The packing may, for instance, be made of plastic or metal.
The contact between the hydrogen-sulphide-absorbing, carbo-nate-containing solution and the hydrogen-sulphide-containing gas is carried out in countercurrent fashion. To this end, each step has means for supplying the carbonate-cont~ining solution through the step countercurrently to the gas, as well as for recycling the solution over the step. As shown in Fig. 1, these means are made up of pumps 10, 11 and 12 which, via conduits 13, 14 and 15, feed the carbonate-cont~ining ~lk~line solution to the respective steps 6, 7 and 8, as well as conduits 16, 17 and 18 which conduct the solution from the respective steps to collecting vessels 19, 20 and 21. From these col-lecting vessels, the solution is recycled over the steps through con-duits 22, 23 and 24, which are connected to the pumps 10, 11 and 12, respectively. Fresh carbonate solution, preferably sodium carbo-nate solution, is fed to the last step 6, as seen in the feed direction of the gas, through a conduit 25 from a supply (not shown) of sodium carbonate solution.
Instead of supplying fresh carbonate solution to the last step, the carbonate solution can be generated in the last step by supplying sodiurn hydroxide solution to this step and allowing the hydroxide WO 95/07750 PCT/SE94/00829 ~
2~7:~3~
solution to absorb carbon dioxide from the gas, such that a carbo-nate-cont~ining solution is obtained according to the reactions (3)-(4) above.
In order to adjust (increase) the pH of the absorption solution, 5 a hydroxide, preferably a sodium hydroxide solution, may be supplied to the collecting vessels 19, 20 and 21 through conduits 26, 27 and 28, respectively, conducting alkali from a supply (not shown), which preferably is common to all the conduits. The supply of sodium hydroxide solution for adjusting the pH of the absorption solution is 10 regulated on the basis of the measured pH values of the solutions in the collecting vessels 19, 20 and 21 (not shown).
As appears from Fig. 1, the different steps are further inter-connected by conduits 29 and 30 for feeding a partial flow of the absorption solution from one step to the preceding step, i.e. from 15 the step 6 to the step 7 as well as from the step 7 to the step 8.
Finally, an outlet conduit 31 is arranged for discharging hydro-gen-sulphide-cont~ining liquid from the collecting vessel 21 and the step 8.
Fig. 2 is a schematic flow chart illustrating the method accord-20 ing to the invention. As indicated in the flow chart, a hydrogen-sul-phide-cont~ining and carbon-dioxide-containing gas 3 is, in a first stage, treated in an apparatus which includes a container 1 for the absorption of hydrogen sulphide, as described in the foregoing with reference to Fig. 1. According to the invention, the absorption of 25 hydrogen sulphide is not, in the first stage, carried out to 100%, i.e.
total absorption of hydrogen sulphide in the first stage, but only so far that at least the main part of the hydrogen sulphide, i.e. at least 50%, preferably about 60-97%, more preferably about 80-95% and most preferred about 90%, of the hydrogen sulphide is absorbed in the first 30 stage. Preferably, a total of at least about 98% of the hydrogen-sul-phide content of the gas is absorbed by the first and the second stage.
The thus-cleaned gas 5, which still contains hydrogen sulphide and carbon dioxide, is then fed from the first stage to the second stage, in which the gas is first combusted in order to convert hydro-35 gen sulphide to sulphur dioxide, and then wet-cleaned in a scrubber in view of the absorption of the sulphur dioxide formed.
~ WO 95/07750 PCTISE94/00829 I ~17~3~2 As indicated in Fig. 2, the combustion takes place in a combus-tion device 32, which has combustion means 33, e.g. a burner, for combusting the gas 5 supplied through an inlet 34 and oxidising the hydrogen sulphide to sulphur dioxide. As mentioned in the foregoing, the combustion device 32 may consist of existing equipment, such as a bark burning boiler or a lime sludge reburning kiln. The sulphur-dioxide-containing flue gas is discharged through an outlet 35 and conducted to a wet cleaner 36, which comprises a container 37 having an inlet 38 for the sulphur-dioxide-containing gas, an outlet 39 for the cleaned gas 40, and means 41 for supplying an alkali-cont~ining solution. As mentioned above, the alkali-containing solution contains a hydroxide of an alkali metal or ~lk~line-earth metal, preferably sodium hydroxide. The solution is circulated by means of a pump 42 to nozzles 43, where it is finely divided and is countercurrently brought into contact with the sulphur-dioxide-cont~ining gas, such that the sulphur dioxide is absorbed by the solution. In order to opti-mise the absorption of sulphur dioxide, without any competing absorption of carbon dioxide, the pH of the solution is adjusted to about 6-8, preferably 7-7.5. The solution that has absorbed sulphur dio~ide is discharged from the second stage at 44.
The invention will now be further elucidated with the aid of a non-restricting Example.
F~x~rnple A test was performed for the selective removal of hydrogen sul-phide from a gas generated in black-liquor evaporation. Use was made of an apparatus of the type described above and shown in Figs 1 and 2.
In the first stage of the method, the absorption of hydrogen sul-phide took place at atmospheric pressure, and the feed gas had a temperature of about 60C and contained 1.13 mole % of hydrogen - sulphide and 16.9 mole % of carbon dioxide. The gas was saturated with water vapour at the temperature at issue, which corresponded to about 18.7 mole % of water. The feed gas flow was 38280 Nm3/h, giving the gas a velocity of about 3.1 m/ s in the absorption tower. The absorption tower had a height of 6.25 m, and the two first steps each had a height of 1.5 m, whereas the last step, as seen in the feed direction of the gas, had a height of 1 m. Each step was provided with WO 95/07750 2 ~ 71`~ 4 ~ PCT/SE94/00829 a packing of the type Mellapack 500 from Sulzer. The diameter of the tower was 2.3 m.
Fresh absorption solution, which consisted of 8.8 m3/h of 2 M
sodium carbonate solution having a temperature of about 60C, was supplied to the last step in the tower along with recycled absorption solution, such that a total of about 50 m3/h of absorption solution was supplied to the last step in the tower. The pH of the absorption solution supplied was about 11.0, which was reduced to about 10.2 during the passage of the solution through the step owing to the 10 absorption of hydrogen sulphide. After passing through the step, the solution was supplied to a 1.5 m3 collecting vessel, where the solution was regenerated by the addition of a 2.5 M sodium hydroxide solution having a temperature of about 60C, such that the pH of the solution was again increased to about 11Ø Then, the regenerated solution 15 was recycled by means of a pump to the last step in the absorption tower for renewed absorption of hydrogen sulphide.
About 11 m3/h of the absorption solution was drawn off from the collecting vessel to the collecting vessel of the intermediate step, whence about 50 m3/h of the absorption solution having a pH of 20 about 11.0 was pumped, as in the previous step, to the intermediate step, whence the absorption solution was drawn off at a pH of about 10.2 to be recycled to the collecting vessel. In the collecting vessel, the solution was regenerated by the addition of a 2.5 M sodium hydroxide solution having a temperature of about 60C, as in the previous step.
From the collecting vessel of the intermediate step, about 13.5 m3/h of the absorption solution was drawn off to the collecting vessel of the first (lowermost) step, whence 50 m3/h of the absorption solution having a pH of about 11.0 was pumped to the first step, as seen in the feed direction of the gas. After passing this step and there 30 absorbing hydrogen sulphide, the solution, now having a pH of about 10.2, was drawn off to be recycled to the collecting vessel. In the col-lecting vessel, the solution was regenerated as in the previous steps by the addition of a 2.5 M sodium hydroxide solution having a tempe-rature of about 60C, such that the pH of the regenerated solution 35 was about 11Ø All in all, about 8.6 m3/h of the 2.5 M sodium hydroxide solution was added to the collecting vessels of the three steps.
~ WO 95/07750 PCT/SE94/00829 2~7~2 From the collecting vessel of the first (lowermost) step, about 17.4 m3/h of the solution having a HS- concentration of 1 mole/l was drawn off. The gas leaving the absorption tower contained 0.113 mole % of hydrogen sulphide and 16.4 mole % of carbon dioxide. In the 5 first stage of the method, the degree of separation of hydrogen sul-phide was about 90%, and the selectivity to hydrogen sulphide in the separation was about 0.67%.
Then came the second stage of the method. Thus, the gas leav-ing the absorption tower in the first stage was combusted in a fur-nace to which was added 31700 Nm3/h of air, which resulted in 66000 Nm3/ h of flue gas cont~ining 650 ppm of SO2 (1930 mole/h).
This flue gas was conducted to an SO2 scrubber of conventional type desclibed in the foregoing. In the scrubber, 1.54 m3/h of the 2.5 M
sodium hydroxide solution was spent, and 2.0 m3/h of fresh water was in addition supplied to the scrubber in order to cool the incoming flue gas to saturation temperature. The gas leaving the scrubber had an So2 concentration of 12 ppm, which corresponded to 35 mole/h (1.12 kg/h of sulphur). The supplied absorption solution was kept at a constant pH of 7.2. The absorption solution was recycled in th scrubber at a total flow rate of 170 m3/h. From the scrubber was drawn off 1.8 m3/h of the solution, which had a total sulphur con-centration (S032- + HSO3- + S042-) of 1.05 mole/l. The total degree of separation of sulphur, i.e. the degree of separation of hydrogen sulphide in the first stage plus the degree of separation of sulphur dioxide in the second stage, thus was 99.8%. In the first stage, 860 kg/h of sodium hydroxide was spent, and in the second stage, 152 kg/h of sodium hydroxide was spent, i.e. a total of 1012 kg/h of NaOH was spent in order to obtain a degree of separation of sulphur of 99.8%.
For comparative purposes, the method was repeated, but this time only with the first stage, i.e. the combustion of hydrogen sul-phide to sulphur dioxide and the absorption of the formed sulphur dioxide in a wet scrubber were not performed. Instead, the separation of hydrogen sulphide in the first stage was carried out to such an extent that 98% of the hydrogen sulphide was separated. The selec-tivity to hydrogen sulphide in a 90-98% separation of hydrogen sul-phide is 0.15. The total selectivity for the whole stage then is about WO 95/07750 21 7 ~ 3 4 2 PCT/SE94/00829 ' . . , NaOH consumption more than 70% higher than in the inventive method, despite the fact that the total degree of separation of sulphur was lower.
Claims (10)
1. A method for selectively removing, by liquid absorption, hydrogen sulphide from a gas (3) containing both hydrogen sulphide and carbon dioxide, c h a r a c t e r i s e d in that the gas (3), in a first stage for removing the main part of the hydrogen-sulphide con-tent of the gas, is contacted in at least one step (6, 7, 8) with a carbo-nate-containing alkaline solution (25) whose pH is adjusted during the absorption by the addition of a hydroxide (26, 27, 28), and that the gas is thereafter combusted in a second stage in order to convert the remaining hydrogen sulphide to sulphur dioxide, which is absorb-ed in an aqueous solution whose pH is adjusted by the addition of alkaline solution or alkaline substance.
2.A method as claimed in claim 1, c h a r a c t e r i s e d in that the gas (3), in said first stage, is contacted with a solution (25) containing sodium carbonate.
3.A method as claimed in claim 2, c h a r a c t e r i s e d in that the gas (3) is contacted with green liquor, white liquor or weak liquor, especially green liquor.
4.A method as claimed in claim 1, c h a r a c t e r i s e d in that the pH of the carbonate-containing alkaline solution is adjust-ed in said first stage by means of a liquid (26, 27, 28) containing alkali metal hydroxide.
5.A method as claimed in claim 4, c h a r a c t e r i s e d in that the pH is adjusted by means of white liquor, green liquor or weak liquor, preferably white liquor or weak liquor, especially white liquor.
6. A method as claimed in any one of the preceding claims, c h a r a c t e r i s e d in that the gas, in said first stage, is con-tacted with the carbonate-containing solution (25) at a pH of about 9-12, preferably about 10-11.
7. A method as claimed in any one of the preceding claims, c h a r a c t e r i s e d in that the gas, in said second stage after the combustion, is absorbed in the aqueous solution at a pH of about 6-8, preferably about 7.0-7.5.
8. A method as claimed in any one of the preceding claims, c h a r a c t e r i s e d in that about 60-97%, preferably about 80-95%, of the hydrogen-sulphide content of the gas is removed in the first stage.
9. A method as claimed in any one of the preceding claims, c h a r a c t e r i s e d in that in all at least about 98% of the hydrogen-sulphide content of the gas is removed.
10. An apparatus for selectively removing, by liquid absorption, hydrogen sulphide from a gas (3) containing both hydrogen sulphide and carbon dioxide, c h a r a c t e r i s e d in that it comprises a) a container (1) having a gas inlet (2) and a gas outlet (4) and containing a packing (9) arranged in a number of successive steps (6, 7, 8); means (25) for supplying a carbonate-containing solution to the last step, as seen in the feed direction of the gas, each step having means for supplying the carbonate-containing solution through the step countercurrently to the gas and for recycling the solution over the step; conduits (29, 30) arranged between the steps for supplying a partial flow of the solution from one step to a preceding step, as seen in the feed direction of the gas; means (26, 27, 28) for supplying a hydroxide to the carbonate-containing solution in at least one of the steps (6, 7, 8); and an outlet conduit (31) from the first step, as seen in the feed direction of the gas, for discharging liquid containing hydrogen sulphide, b) a combustion device (32) having an inlet (34) for hydrogen-sulphide-containing gas (5) from the gas outlet (4) of the container (1), combustion means (33) for combusting the gas supplied and con-verting the hydrogen sulphide therein to sulphur dioxide, and an outlet (35) for discharging sulphur-dioxide-containing gas from the combustion device (32), and c) a wet cleaner (36) adapted to absorb the sulphur dioxide formed upon combustion, and comprising a container (37) which has an inlet (38) for sulphur-dioxide-containing gas from the combustion device (32); an outlet (39) for cleaned gas (40); means (41, 42, 43) for supplying, circulating and finely dividing an aqueous solution, whose pH is adjusted by the addition of an alkaline solution or alkaline sub-stance, so as to contact it with the sulphur-dioxide-containing gas supplied; and means (44) for discharging solution that has absorbed sulphur dioxide.
Applications Claiming Priority (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| SE9303034A SE501782C2 (en) | 1993-09-17 | 1993-09-17 | Method and apparatus for selectively removing hydrogen sulfide from a gas |
| SE9303034-4 | 1993-09-17 |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CA2171342A1 true CA2171342A1 (en) | 1995-03-23 |
Family
ID=20391129
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CA002171342A Abandoned CA2171342A1 (en) | 1993-09-17 | 1994-09-07 | Method and apparatus for absorbing hydrogen sulphide |
Country Status (10)
| Country | Link |
|---|---|
| JP (1) | JPH09502651A (en) |
| CN (1) | CN1066634C (en) |
| AU (1) | AU7712594A (en) |
| BR (1) | BR9407636A (en) |
| CA (1) | CA2171342A1 (en) |
| FI (1) | FI961237A7 (en) |
| NO (1) | NO305277B1 (en) |
| RU (1) | RU2119375C1 (en) |
| SE (1) | SE501782C2 (en) |
| WO (1) | WO1995007750A1 (en) |
Families Citing this family (23)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH09183618A (en) * | 1995-12-28 | 1997-07-15 | Kansai Electric Power Co Inc:The | Production of gypsum |
| RU2176266C1 (en) * | 2000-03-27 | 2001-11-27 | Дочернее открытое акционерное общество "Гипрогазцентр" | Method of treatment and dehydration of natural and associated petroleum gas with high content of hydrogen sulfide |
| RU2201792C2 (en) * | 2001-05-28 | 2003-04-10 | Открытое акционерное общество "АВИСМА титано-магниевый комбинат" | Method of treating titanium-magnesium production effluent gases |
| RU2331461C2 (en) * | 2003-09-09 | 2008-08-20 | Флуор Корпорейшн | Improved use and solovent recovery |
| FI119915B2 (en) * | 2003-10-03 | 2011-06-15 | Metsae Botnia Ab Oy | Removal of sulfur from the smell gases of a cellulose factory |
| CA2455011C (en) | 2004-01-09 | 2011-04-05 | Suncor Energy Inc. | Bituminous froth inline steam injection processing |
| FI118629B (en) * | 2005-06-15 | 2008-01-31 | Metso Power Oy | Method and apparatus for removing carbon dioxide from flue gases containing sulfur dioxide |
| RU2320398C2 (en) * | 2006-04-13 | 2008-03-27 | Общество с ограниченной ответственностью Нефтегаз-Сталь Экспертно-научно-внедренческая компания ООО "НЕФТЕГАЗ-СТАЛЬ-ЭНВК" | Method of removing hydrocarbon product from hydrogen sulfide |
| US7964170B2 (en) | 2007-10-19 | 2011-06-21 | Fluegen, Inc. | Method and apparatus for the removal of carbon dioxide from a gas stream |
| RU2394635C2 (en) * | 2008-06-16 | 2010-07-20 | Юрий Викторович Кушелев | Method of gas cleaning and device to this end |
| DE102008062387A1 (en) * | 2008-12-17 | 2010-07-01 | Uhde Gmbh | Process for the purification of industrial gases and production of sour gases |
| AU2012208952B2 (en) * | 2011-01-18 | 2017-01-05 | Commonwealth Scientific And Industrial Research Organisation | Process for capturing acid gases |
| CN102895862B (en) * | 2012-10-25 | 2014-12-17 | 四川皇龙智能破碎技术股份有限公司 | Method and system for removing hydrogen sulfide from coal gas through single tower |
| CN103381334B (en) * | 2013-07-17 | 2015-07-15 | 山东大学 | Method and device for removing hydrogen sulfide through steel slag |
| CN103436301B (en) * | 2013-09-13 | 2015-02-25 | 上海电力学院 | Combined dust removal and desulfurization system for coal gas |
| CN104492227B (en) * | 2014-12-11 | 2016-09-14 | 西安长庆科技工程有限责任公司 | A kind of for processing containing H2the absorption of S-acid gas and CIU and method |
| CN104984652A (en) * | 2015-07-11 | 2015-10-21 | 河北新启元能源技术开发股份有限公司 | Treating device for tail gas in acidifying refinement of alkaline residues and treating process thereof |
| CN105293852B (en) * | 2015-12-04 | 2017-08-25 | 山西省生态环境研究中心 | The method of the synchronous coupling odor purification of sludge organism leaching conditioning |
| US10370176B2 (en) * | 2017-09-12 | 2019-08-06 | Wd-40 Company | Child resistant aerosol actuator |
| CN108671701A (en) * | 2018-05-17 | 2018-10-19 | 浙江卫星能源有限公司 | A kind of sulfur method of hydrogen sulfide containing gas |
| CN109589760B (en) * | 2018-11-07 | 2021-04-27 | 合肥通用机械研究院有限公司 | Device and method for rapidly treating hydrogen sulfide for laboratory |
| KR102466873B1 (en) * | 2021-03-29 | 2022-11-17 | 주식회사 시뮬레이션테크 | CO2 Reduction Equipment Using Scrubber For Ship |
| CN114452803B (en) * | 2022-01-12 | 2023-03-24 | 中国科学院过程工程研究所 | Method and system for treating pyrolysis gas generated by pyrolysis of waste tires |
Family Cites Families (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| SE47516C1 (en) * | 1920-01-01 | |||
| US3236589A (en) * | 1961-02-03 | 1966-02-22 | Reinhall Rolf Bertil | Method of working up cellulose waste liquor containing sodium and sulfur |
| SE448173B (en) * | 1985-06-03 | 1987-01-26 | Croon Inventor Ab | PROCEDURE FOR THE RECOVERY OF CELLULOSA DISPOSAL CHEMICALS BY PYROLYSIS |
| US5284550A (en) * | 1992-06-18 | 1994-02-08 | Combustion Engineering, Inc. | Black liquier gasification process operating at low pressures using a circulating fluidized bed |
| SE470516B (en) * | 1992-11-05 | 1994-06-27 | Chemrec Ab | Purifying gas from the gasification of black liquor |
| SE9300533L (en) * | 1993-02-18 | 1994-08-19 | Flaekt Ab | Methods and apparatus for the absorption of hydrogen sulphide |
-
1993
- 1993-09-17 SE SE9303034A patent/SE501782C2/en not_active IP Right Cessation
-
1994
- 1994-09-07 CA CA002171342A patent/CA2171342A1/en not_active Abandoned
- 1994-09-07 BR BR9407636A patent/BR9407636A/en not_active IP Right Cessation
- 1994-09-07 RU RU96108406A patent/RU2119375C1/en not_active IP Right Cessation
- 1994-09-07 AU AU77125/94A patent/AU7712594A/en not_active Abandoned
- 1994-09-07 JP JP7509118A patent/JPH09502651A/en active Pending
- 1994-09-07 WO PCT/SE1994/000829 patent/WO1995007750A1/en not_active Ceased
- 1994-09-07 CN CN94193932A patent/CN1066634C/en not_active Expired - Fee Related
-
1996
- 1996-03-13 NO NO961016A patent/NO305277B1/en not_active IP Right Cessation
- 1996-03-15 FI FI961237A patent/FI961237A7/en not_active IP Right Cessation
Also Published As
| Publication number | Publication date |
|---|---|
| SE9303034D0 (en) | 1993-09-17 |
| RU2119375C1 (en) | 1998-09-27 |
| JPH09502651A (en) | 1997-03-18 |
| NO961016L (en) | 1996-03-13 |
| FI961237A0 (en) | 1996-03-15 |
| NO305277B1 (en) | 1999-05-03 |
| SE9303034L (en) | 1995-03-18 |
| CN1133568A (en) | 1996-10-16 |
| SE501782C2 (en) | 1995-05-15 |
| NO961016D0 (en) | 1996-03-13 |
| FI961237A7 (en) | 1996-03-15 |
| CN1066634C (en) | 2001-06-06 |
| BR9407636A (en) | 1997-01-28 |
| AU7712594A (en) | 1995-04-03 |
| WO1995007750A1 (en) | 1995-03-23 |
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