CA1125477A - Production of lead monoxide from lead sulfate with acetic acid - Google Patents
Production of lead monoxide from lead sulfate with acetic acidInfo
- Publication number
- CA1125477A CA1125477A CA337,238A CA337238A CA1125477A CA 1125477 A CA1125477 A CA 1125477A CA 337238 A CA337238 A CA 337238A CA 1125477 A CA1125477 A CA 1125477A
- Authority
- CA
- Canada
- Prior art keywords
- lead
- carbonate
- solution
- monoxide
- acetic acid
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired
Links
- QTBSBXVTEAMEQO-UHFFFAOYSA-N Acetic acid Chemical compound CC(O)=O QTBSBXVTEAMEQO-UHFFFAOYSA-N 0.000 title claims abstract description 143
- YEXPOXQUZXUXJW-UHFFFAOYSA-N oxolead Chemical compound [Pb]=O YEXPOXQUZXUXJW-UHFFFAOYSA-N 0.000 title claims abstract description 95
- PIJPYDMVFNTHIP-UHFFFAOYSA-L lead sulfate Chemical compound [PbH4+2].[O-]S([O-])(=O)=O PIJPYDMVFNTHIP-UHFFFAOYSA-L 0.000 title claims abstract description 28
- 238000004519 manufacturing process Methods 0.000 title abstract description 9
- 229910000003 Lead carbonate Inorganic materials 0.000 claims abstract description 79
- MFEVGQHCNVXMER-UHFFFAOYSA-L 1,3,2$l^{2}-dioxaplumbetan-4-one Chemical compound [Pb+2].[O-]C([O-])=O MFEVGQHCNVXMER-UHFFFAOYSA-L 0.000 claims abstract description 75
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 claims abstract description 72
- 229940046892 lead acetate Drugs 0.000 claims abstract description 42
- ATRRKUHOCOJYRX-UHFFFAOYSA-N Ammonium bicarbonate Chemical compound [NH4+].OC([O-])=O ATRRKUHOCOJYRX-UHFFFAOYSA-N 0.000 claims abstract description 41
- 239000001099 ammonium carbonate Substances 0.000 claims abstract description 41
- 235000012501 ammonium carbonate Nutrition 0.000 claims abstract description 41
- 229910002092 carbon dioxide Inorganic materials 0.000 claims abstract description 36
- 239000001569 carbon dioxide Substances 0.000 claims abstract description 33
- 239000000463 material Substances 0.000 claims abstract description 24
- YADSGOSSYOOKMP-UHFFFAOYSA-N dioxolead Chemical compound O=[Pb]=O YADSGOSSYOOKMP-UHFFFAOYSA-N 0.000 claims description 41
- 239000007787 solid Substances 0.000 claims description 31
- 238000000034 method Methods 0.000 claims description 29
- 230000008569 process Effects 0.000 claims description 28
- 239000002002 slurry Substances 0.000 claims description 22
- 229910052921 ammonium sulfate Inorganic materials 0.000 claims description 20
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 claims description 19
- 235000011130 ammonium sulphate Nutrition 0.000 claims description 19
- 238000010438 heat treatment Methods 0.000 claims description 12
- 239000012535 impurity Substances 0.000 claims description 11
- 239000006227 byproduct Substances 0.000 claims description 10
- QTBSBXVTEAMEQO-UHFFFAOYSA-M Acetate Chemical compound CC([O-])=O QTBSBXVTEAMEQO-UHFFFAOYSA-M 0.000 claims description 7
- 229910001868 water Inorganic materials 0.000 claims description 7
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 6
- 239000003638 chemical reducing agent Substances 0.000 claims description 5
- 239000006185 dispersion Substances 0.000 claims description 2
- 229940112735 lead carbonate Drugs 0.000 claims 26
- 238000010924 continuous production Methods 0.000 claims 1
- 239000000376 reactant Substances 0.000 claims 1
- KEQXNNJHMWSZHK-UHFFFAOYSA-L 1,3,2,4$l^{2}-dioxathiaplumbetane 2,2-dioxide Chemical compound [Pb+2].[O-]S([O-])(=O)=O KEQXNNJHMWSZHK-UHFFFAOYSA-L 0.000 abstract 1
- 239000000243 solution Substances 0.000 description 62
- HTUMBQDCCIXGCV-UHFFFAOYSA-N lead oxide Chemical compound [O-2].[Pb+2] HTUMBQDCCIXGCV-UHFFFAOYSA-N 0.000 description 47
- 229940059913 ammonium carbonate Drugs 0.000 description 33
- 229910000464 lead oxide Inorganic materials 0.000 description 15
- 238000006243 chemical reaction Methods 0.000 description 13
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 11
- 239000000047 product Substances 0.000 description 9
- 150000002611 lead compounds Chemical class 0.000 description 8
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 description 6
- 238000001354 calcination Methods 0.000 description 6
- 239000003153 chemical reaction reagent Substances 0.000 description 6
- WABPQHHGFIMREM-UHFFFAOYSA-N lead(0) Chemical compound [Pb] WABPQHHGFIMREM-UHFFFAOYSA-N 0.000 description 6
- 239000002562 thickening agent Substances 0.000 description 6
- 229910021529 ammonia Inorganic materials 0.000 description 5
- 230000009850 completed effect Effects 0.000 description 4
- 238000011437 continuous method Methods 0.000 description 4
- 238000000354 decomposition reaction Methods 0.000 description 4
- UWRBYRMOUPAKLM-UHFFFAOYSA-L lead arsenate Chemical compound [Pb+2].O[As]([O-])([O-])=O UWRBYRMOUPAKLM-UHFFFAOYSA-L 0.000 description 4
- MOUPNEIJQCETIW-UHFFFAOYSA-N lead chromate Chemical compound [Pb+2].[O-][Cr]([O-])(=O)=O MOUPNEIJQCETIW-UHFFFAOYSA-N 0.000 description 4
- BDAGIHXWWSANSR-UHFFFAOYSA-N methanoic acid Natural products OC=O BDAGIHXWWSANSR-UHFFFAOYSA-N 0.000 description 4
- 230000001590 oxidative effect Effects 0.000 description 4
- 238000001556 precipitation Methods 0.000 description 4
- 238000000926 separation method Methods 0.000 description 4
- 238000011282 treatment Methods 0.000 description 4
- 150000001242 acetic acid derivatives Chemical class 0.000 description 3
- 239000000706 filtrate Substances 0.000 description 3
- 239000007789 gas Substances 0.000 description 3
- 239000002198 insoluble material Substances 0.000 description 3
- 239000007788 liquid Substances 0.000 description 3
- 150000003839 salts Chemical class 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 239000002699 waste material Substances 0.000 description 3
- OSWFIVFLDKOXQC-UHFFFAOYSA-N 4-(3-methoxyphenyl)aniline Chemical compound COC1=CC=CC(C=2C=CC(N)=CC=2)=C1 OSWFIVFLDKOXQC-UHFFFAOYSA-N 0.000 description 2
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 2
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 2
- BVKZGUZCCUSVTD-UHFFFAOYSA-L Carbonate Chemical compound [O-]C([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-L 0.000 description 2
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 2
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 2
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N Iron oxide Chemical compound [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 description 2
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 2
- 238000003723 Smelting Methods 0.000 description 2
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 2
- 239000007864 aqueous solution Substances 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 229910052791 calcium Inorganic materials 0.000 description 2
- 229910052799 carbon Inorganic materials 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- XJUNRGGMKUAPAP-UHFFFAOYSA-N dioxido(dioxo)molybdenum;lead(2+) Chemical compound [Pb+2].[O-][Mo]([O-])(=O)=O XJUNRGGMKUAPAP-UHFFFAOYSA-N 0.000 description 2
- NKTZYSOLHFIEMF-UHFFFAOYSA-N dioxido(dioxo)tungsten;lead(2+) Chemical compound [Pb+2].[O-][W]([O-])(=O)=O NKTZYSOLHFIEMF-UHFFFAOYSA-N 0.000 description 2
- 238000000605 extraction Methods 0.000 description 2
- 235000019253 formic acid Nutrition 0.000 description 2
- -1 lead sulfate Chemical class 0.000 description 2
- 239000002184 metal Substances 0.000 description 2
- 229910052751 metal Inorganic materials 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 239000002994 raw material Substances 0.000 description 2
- 230000035484 reaction time Effects 0.000 description 2
- USFZMSVCRYTOJT-UHFFFAOYSA-N Ammonium acetate Chemical compound N.CC(O)=O USFZMSVCRYTOJT-UHFFFAOYSA-N 0.000 description 1
- 239000005695 Ammonium acetate Substances 0.000 description 1
- DJHGAFSJWGLOIV-UHFFFAOYSA-K Arsenate3- Chemical class [O-][As]([O-])([O-])=O DJHGAFSJWGLOIV-UHFFFAOYSA-K 0.000 description 1
- 229910000978 Pb alloy Inorganic materials 0.000 description 1
- 229910001245 Sb alloy Inorganic materials 0.000 description 1
- QHNORJFCVHUPNH-UHFFFAOYSA-L To-Pro-3 Chemical compound [I-].[I-].S1C2=CC=CC=C2[N+](C)=C1C=CC=C1C2=CC=CC=C2N(CCC[N+](C)(C)C)C=C1 QHNORJFCVHUPNH-UHFFFAOYSA-L 0.000 description 1
- 229910000004 White lead Inorganic materials 0.000 description 1
- 239000006096 absorbing agent Substances 0.000 description 1
- 230000002730 additional effect Effects 0.000 description 1
- 229910052783 alkali metal Inorganic materials 0.000 description 1
- 150000001340 alkali metals Chemical class 0.000 description 1
- 229940043376 ammonium acetate Drugs 0.000 description 1
- 235000019257 ammonium acetate Nutrition 0.000 description 1
- 239000000908 ammonium hydroxide Substances 0.000 description 1
- 229910052787 antimony Inorganic materials 0.000 description 1
- 239000002140 antimony alloy Substances 0.000 description 1
- WATWJIUSRGPENY-UHFFFAOYSA-N antimony atom Chemical compound [Sb] WATWJIUSRGPENY-UHFFFAOYSA-N 0.000 description 1
- QQHJESKHUUVSIC-UHFFFAOYSA-N antimony lead Chemical compound [Sb].[Pb] QQHJESKHUUVSIC-UHFFFAOYSA-N 0.000 description 1
- 229910000410 antimony oxide Inorganic materials 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 239000011575 calcium Substances 0.000 description 1
- 239000001639 calcium acetate Substances 0.000 description 1
- 229960005147 calcium acetate Drugs 0.000 description 1
- 235000011092 calcium acetate Nutrition 0.000 description 1
- ZCDOYSPFYFSLEW-UHFFFAOYSA-N chromate(2-) Chemical class [O-][Cr]([O-])(=O)=O ZCDOYSPFYFSLEW-UHFFFAOYSA-N 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 239000002657 fibrous material Substances 0.000 description 1
- 239000012065 filter cake Substances 0.000 description 1
- 150000004675 formic acid derivatives Chemical class 0.000 description 1
- 229910052949 galena Inorganic materials 0.000 description 1
- 238000009854 hydrometallurgy Methods 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-M hydroxide Chemical compound [OH-] XLYOFNOQVPJJNP-UHFFFAOYSA-M 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- 229940056932 lead sulfide Drugs 0.000 description 1
- 229910052981 lead sulfide Inorganic materials 0.000 description 1
- 229910021514 lead(II) hydroxide Inorganic materials 0.000 description 1
- XCAUINMIESBTBL-UHFFFAOYSA-N lead(ii) sulfide Chemical compound [Pb]=S XCAUINMIESBTBL-UHFFFAOYSA-N 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 150000002826 nitrites Chemical class 0.000 description 1
- 230000001473 noxious effect Effects 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- VTRUBDSFZJNXHI-UHFFFAOYSA-N oxoantimony Chemical compound [Sb]=O VTRUBDSFZJNXHI-UHFFFAOYSA-N 0.000 description 1
- 239000004033 plastic Substances 0.000 description 1
- 229920003023 plastic Polymers 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 238000011946 reduction process Methods 0.000 description 1
- 238000007670 refining Methods 0.000 description 1
- 239000013049 sediment Substances 0.000 description 1
- 239000000377 silicon dioxide Substances 0.000 description 1
- XTQHKBHJIVJGKJ-UHFFFAOYSA-N sulfur monoxide Chemical class S=O XTQHKBHJIVJGKJ-UHFFFAOYSA-N 0.000 description 1
- 229910052815 sulfur oxide Inorganic materials 0.000 description 1
- 239000006228 supernatant Substances 0.000 description 1
- 239000010414 supernatant solution Substances 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01G—COMPOUNDS CONTAINING METALS NOT COVERED BY SUBCLASSES C01D OR C01F
- C01G21/00—Compounds of lead
- C01G21/02—Oxides
- C01G21/06—Lead monoxide [PbO]
-
- H—ELECTRICITY
- H01—ELECTRIC ELEMENTS
- H01M—PROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
- H01M10/00—Secondary cells; Manufacture thereof
- H01M10/54—Reclaiming serviceable parts of waste accumulators
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01P—INDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
- C01P2002/00—Crystal-structural characteristics
- C01P2002/70—Crystal-structural characteristics defined by measured X-ray, neutron or electron diffraction data
- C01P2002/72—Crystal-structural characteristics defined by measured X-ray, neutron or electron diffraction data by d-values or two theta-values, e.g. as X-ray diagram
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01P—INDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
- C01P2006/00—Physical properties of inorganic compounds
- C01P2006/60—Optical properties, e.g. expressed in CIELAB-values
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01P—INDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
- C01P2006/00—Physical properties of inorganic compounds
- C01P2006/80—Compositional purity
-
- 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
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/84—Recycling of batteries or fuel cells
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Inorganic Chemistry (AREA)
- Engineering & Computer Science (AREA)
- Manufacturing & Machinery (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Electrochemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Manufacture And Refinement Of Metals (AREA)
- Secondary Cells (AREA)
- Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)
- Inorganic Compounds Of Heavy Metals (AREA)
Abstract
PRODUCTION OF LEAD MONOXIDE FROM LEAD SULFATE WITH ACETIC ACID
ABSTRACT:
An efficient and inexpensive method for producing lead monoxide from lead sulfate bearing materials such as recycled battery mud is provided comprising:
(a) reacting said material with an ammonium carbonate solution to convert lead sulfate to lead carbonate;
(b) decomposing the lead carbonate to form impure lead monoxide;
(c) reacting the impure lead monoxide with acetic acid to form a lead acetate solution;
(d) contacting the lead acetate solution with carbon dioxide to produce insoluble lead carbonate; and (e) decomposing the lead carbonate to form lead monoxide.
ABSTRACT:
An efficient and inexpensive method for producing lead monoxide from lead sulfate bearing materials such as recycled battery mud is provided comprising:
(a) reacting said material with an ammonium carbonate solution to convert lead sulfate to lead carbonate;
(b) decomposing the lead carbonate to form impure lead monoxide;
(c) reacting the impure lead monoxide with acetic acid to form a lead acetate solution;
(d) contacting the lead acetate solution with carbon dioxide to produce insoluble lead carbonate; and (e) decomposing the lead carbonate to form lead monoxide.
Description
112S47~
This invention is concerned with a process for preparing lead monoxide from impure lead sulfate bearing materials, particularly impure lead sulfate bearing materials such as recycled battery mud.
In the past, lead oxide has been produced by the oxidation of lead metal in a Barton Pot. The greatest single expense of the total manufacturing cost of producing lead monoxide is the cost of the lead metal. Such lead metal may be obtained by re-ducing reclaimed lead compounds such as lead sulfate, lead oxide and lead alloys from used battery plates. Not only is such ]ead oxide production costly but also involves the formation of noxious sulfur oxides as by-products which is environmentally unsatis-factory. Accordingly, there is substantial need for a process of producing pure lead monoxide from an inexpensive lead bearing material such as battery mud short of reducing lead compounds therein; refining the metal and oxidizing the so-formed lead metal.
In U.S. Patent No. 720,670 to A. C. J. Charlier, a method for producing white lead (lead carbonate) from litharge or lead oxide is provided comprising acidifying the oxide and contacting it with carbon dioxide gas under pressure.
In U.S. Patent No. 1,916,302 to L. P. Curtin, a process for recovering lead in the form of an acetate directly from lead ores, particularly lead sulfide containing galena ore is described.
The process comprises roasting the ore by the air-reduction pro-cess, to yield a product containing lead oxide, lead sulfate and basic lead sulfate, extracting the product with a solution of lead acetat~ to remove lead oxide values and extracting the residue from the lead acetate extraction with calcium or a~onium acetate to remove the lead sulfate values. The lead oxide dissolved in the lead acetate solution forms basic lead acetate .
:
~lZ547~
and may readily be precipitated by means of carbon dioxide as basic or normal lead carbonate. The lead carbonate may in turn be converted into lead monoxide by heating from 400C. to 475C.
Insoluble lead salts such as lead chromate or lead arsenate may be precipitated from the calcium or ammonium acetate solution after extraction.
In U.S. Patent No. 2,328,089 to J. J. Mulligan, a process is described for recovering soluble lead salts from raw materials such as insoluble lead compounds and impure lead bearing materials, e.g., lead sulfate, lead oxide, lead peroxide, spent litharge, old battery lead plates and lead battery mud or sediment. The soluble lead salts are suitable for the manufacture of lead com-pounds, such as lead arsenates, chromates, molybdates, tungstates, and acetates.
The aforementioned prior art process comprises first adding an aqueous solution of an alkali metal or ammonium carbonate or hydroxide to the raw material to convert the lead compound therein to an insoluhle lead compound. The insoluble residue from this addition is next treated with formic acid or acetic acid wherein ~Othe acetic acid preferably contains a reducing agent for lead peroxide contained in the residue, e.g., formic acid, nitrite salts, hydrogen peroxide, and hydrochloric acid. This treatment converts the insoluble lead compound to soluble acetate and for-mate salts which are in turn combined with appropriate reagents to make lead arsenate, lead chromate, and lead molybdate.
In U.S. Patent No. 3,883,348 to F. A. Acoveno and T. W.
Freudiger, a process for the treatment of lead bearing waste material such as battery mud is provided comprising agitating the waste material in a solution of ammonium carbonate to pro-3 0duce ammonium sulfate and lead carbonate, separating the solids from the liquid and heating the solids to decompose thelead carbonate contained therein to form lead monoxide.
The lead monoxide in combination with lead dioxide con-tained in the solids is used as furnace feed for final reduction to metallic lead. The carbon dioxide released during the carbonate decomposition stage is introduced to a condenser-absorber zone where ammonia and make-up carbon dioxide is added to produce ammonium carbonate.
The ammonium carbonate is then passed back or recycled to the leach solution to desulfate incoming waste material.
The present invention provides a multi-step hydro-metallurgical process for producing substantially pure lead monoxide from inexpensive lead bearing materials such as battery mud which involves the use of inexpensive and recyclable chemical reagents and physical treatments such as heating and solid/liquid separation.
The process of this invention employs a lead bearing material, particularly a lead sulfate bearing material such as battery mud, which may also contain lead oxides and other impurities.
An unexpected process for preparing lead oxide from lead bearing material has been discovered which comprises:
~ a) reacting said material with an ammonium carbonate solution to convert said lead sulfate to lead carbonate;
(b) decomposing substantially all of the lead carbonate to impure lead monoxide by heating at temperatures from about 400 to 650C., (c) reacting the impure lead monoxide with an effective amount of an acetic acid solution to convert said lead mon-oxide to a lead acetate solution;
llZ54~7 (d) separating said lead acetate solution from the insoluble impurities;
(e) contacting the lead acetate solution fro~ step (d) with carbon dioxide gas to form lead carbonate; and (f) decomposing the lead carbonate to produce lead monoxide.
- 4a -Any lead dioxide present in the lead bearing materïal may also be decomposed along with lead carbonate in step (b) of the process to produce additional lead monoxide. Alternatively, such lead dioxide may be treated with acetic acid in step (c) together with a reducing agent to simultaneously decompose the lead dioxide and form additional lead acetate.
In another embodiment of this invention, a continuous method for producing lead monoxide from a lead sulfate bearing material is provided wherein the by-products of reactions 1~ occurring in the above process are used to form the reagents used in the various steps of the process. More particularly, carbon dioxide formed as a by-product of the decomposition of lead carbonate in step (b~ can be separated and combined with ammonia to produce the ammonium carbonate solution used in step (a).
The carbon dioxide formed as a by-product of the decomposition of lead carbonate in step (ej can be recycled for use in step (d).
The acetic acid produced as a by-product in step (d) can be re-cycled for use in step (c).
In addltion, lead chemicals such as lead chromate, lead arsenate, and lead tungstate can be prepared by precipitation fr~m the lead acetate solution formed in step (c) with appro-priate reagents and separating the so-formed lead chemicals from the remaining solution.
Figure 1 is a flow diagram of the continuous method of this invention.
llZS477 The staxting material for the process of this invention is a lead bearing material, particularly a lead sulfate-bearing material such as battery mud. Such battery mud consists mainly of chemically reactive lead compounds such as lead sulfate, and amounts of lead dioxide, lead-antimony alloys and other complex lead bearing compounds. Such battery mud is produced by crush-ing the batteries and separating the battery parts, namely grid metal, plastics,and battery mud fines by well known separatory methods known in the art, from the mud.
~0 According to this invention, the lead bearing material is slurried in water and then leached with an ammonium carbonate solution wherein the lead sulfate contained therein is reacted and converted to insoluble lead carbonate and soluble ammonium sulfate according to the following reaction:
4 (NH4)2Co3 ~ PbC03 + (NH4)2S04 Unreacted materials such as lead dioxide remain undissolved in admixture with the insoluble lead carbonate in the ammonium sulfate solution.
Generally an aqueous solution Gf ammonium carbonate is employed containing from 1.5% to 12.5% ammonium carbonate and preferably about 6.5~. A lead battery mud containing from about 16-18 wt % of sulfate anion can he employed in the first step. Such mud is slurried with water to form a heterogeneous dispersion containing from about 10% to 60% by weight of mud and preferably about 35% by weight. The mud slurry and ammonium carbonate solution are then combined, preferably in counter-current fashion at a mole ratio of ammonium carbonate to lead sulfate in 3~ the mud slurry of from 1:1 to 1.25 at temperatures of from 25C.
llZ5477 to 35C., and preferably 30C. Reaction time may vary from 1 minute to 60 minutes but generally all reactions are com-pleted between 5 and 15 minutes.
After the reaction is substantially completed, the ammonium sulfate solution is separated from the lead carbonate and other insoluble materials by conventional solid/liquid separation techniques. The isolated ammonium sulfate solution may then be crystallized to recover solid ammonium sulfate.
Alternately and more preferably, the ammonium carbonate desulfation of battery mud may be carried out in two stages wherein fresh ammonium carbonate solution is added to the second stage and the ammonium carbonate solution used in the first stage is the unexpended ammonium carbonate solution from the second stage. In this embodiment, virgin battery mud is slurried in the first or primary stage with recovered ammonium carbonate solution from the secondary desulfation stage. The slurry is thickened by removal of supernatant ammonium sulfate solution.
The separated ammonium sulfate solution is then sent to an a~ ammonium sulfate crystallizer for recovery of solid ammonium sulfate. The thickened slurry is then reacted with fresh ammonium carbonate in a secondary stage to convert substantially all lead sulfate in the battery mud to lead carbonate and to form addi-tional ammonium sulfate. The lead carbonate and other insolubles in the form of a slurry is thickened and the thickened slurry is filtered and washed in a horizontal vacuum filter. The solution recovered from the thickener, containing both ammonium carbonate and ammonium sulfate is recycled to the first stage - desulfation above.
The lead carbonate and other insoluble material separated 1:125477 from the desulfation step are next calcined or heated at tempera-tures sufficient to decompose the lead carbonate to lead monoxide and carbon dioxide according to the following reaction:
PbC03 a - 3 PbO + Co2 Generally the temperatures required to decompose the lead carbonate are from 400C. to ~50C., and preferably 600C.
Preferably, the heating should be conducted in an inert atmosphere even though it may be conducted in a slightly oxidizing atmosphere.
Heating is conducted for between about 15 and 90 minutes to con-vert substantially all the lead carbonate to lead monoxide. Most usually, however, all decomposition is completed within 60 minutes. The carbon dioxide evolved may be separated from the lead monoxide and reacted with ammonia to form ammonium carbonate which may in turn be used as the ammonium carbonate leach for desulfation of the battery mud. This will be discussed in more detail in connection with Figure 1 depicting the continuous method of this invention.
Any lead dioxide contained in the insoluble residue after ammonium carbonate treatment may also be decomposed along with the lead carbonate to form additional lead monoxide and oxygen according to the following:
2PbO2 ~ 2PbO + 2 A portion of lead metal contained in the solids is also converted to lead monoxide. The lead monoxide product in ad- -mixture with undecomposed lead dioxide or lead carbonate and 3~ other insoluble materials is leached with an acetic acid solution (HAc). During this acetic acid leach step the lead monoxide reacts with acetic acid to form soluble lead acetate and/or basic lead acetate. While stoichiometric amounts of acetic acid to reactive lead may be employed, best results are achieved at mole ratios of 1:0.9 to 1.1.
PbO + HAc ~ PbAc2 + H2o lead (acetate) ~ or /O 2PbO + 2HAc ~ PbAc2-pb(oH)2 ,basic lead ~ acetate Any undecomposed lead carbonate is converted to soluble lead acetate by acetic acid during the reaction as follows:
PbCO3 + 2HAc - ~ PbAc2 + H20 + CO2 Alternatively to decompose and react lead dioxide in this step, a reducing agent such as hydrogen peroxide may be added with the acetic acid solution to form lead acetate as follows:
~O PbO2 + 2HAc + H2O2 -- ~ PbAc2 + 2H2 + 2 Generally, a 0.1-15 wt %, preferably a 0.5-5 wt % solu-tion of acetic acid is combined with the products of calcination ~ as a water slurry in stoichiometric ratios of 1:0.5 to 1.5 - acetate to reactive lead. The concentration of reactive leàd (lead carbonate, lead oxide and lead dioxide) in the calcined feed is not critical but for efficient operation the lead con-centration should be from 50% to 99% by weight. The solution is contacted with the slurry at a wide range of temperatures.
3D Increasing temperatures above about 15C. results in the _ g _ eoncomitant increase in reaction rate with preferred conditions being atmospheric pressure at temperatures from 25C. to 100C.
Reaction times between 5 and 60 minutes are necessary to com-plete the reaction.
The lead acetate solution formed by the reactions between the acetic acid and lead monoxide, undecomposed lead carbonate, if any, and lead dioxide, if any, plus reducing agent is separated from the insoluble residue containing minor amounts basic lead aeeta~e and antimonial lead gangue. The insoluble residue is then sent to a smelter to recover the antimony-lead values therefrom.
A portion of the separated lead aeetate solution may be used to prepare lead ehemieals such as lead chromate, lead tungstate, lead molybdate, lead arsenate and the like by re-action with appropriate reagents.
In order to prepare substantially pure lead monoxide from the lead acetate solution according to this invention, the lead acetate solution is next contacted with carbon dioxide gas under pressure to precipitate lead carbonate and acetic acid accordin~
to the following reaetion:
PbAc2 + CO2 ~ H2O ~ PbCO3 + 2HAc PbAc2-Pb(OH)2 + 2CO2 ~ ~ 2PbCO3 + 2HAc Generally, the carbon dioxide is bubbled into the lead acetate solution at pressures of from atmospheric to 250 p.s.i.g.
preferably from 20 to 100 p.s.i.g. at temperatures of from about 5C. to 95C., preferably from 40C. to 60C. The carbon 3O dioxide is added in an amount of from 0.5 to 1.2 moles per mole of lead in the lead acetate solution. Generally all conversion to lead carbonate is completed within 60 minutes.
The insoluble lead carbonate is next separated from the acetic acid solution and then calcined at temperatures of from 400 to 800C., preferably from 550 to 650C., in an inert or slightly oxidizing atmosphere for from one minute to reaction completion, to produce substantially pure lead monoxide and carbon dioxide. The vapors from the calcination are partially - condensed to yield an acetic acid solution which can be returned to the leach step. The non-condensed CO2 vapors can be com-pressed and recycled to the lead carbonate precipitation step in the continuous embodiment of this invention as will be shown in more detail below. The term substantially pure as used herein means the product contains less than 1~ impurities such as primary iron oxide and antimony oxide and preferably less than 0.1%
impurities.
Figure 1 shows a process flow diagram of one continuous method according to this invention wherein by-products of various reactions such as carbon dioxide from lead carbonate calcination, acetic acid from the lead acetate carbonation, and carbon dioxide from the lead carbonate calcination are recycled or used to prepare reagents used in the process.
A battery mud feed 11 containing lead sulfate, lead dioxide and other materials is leached with ammonium carbonate solution 12. The products, comprising an ammonium carbonate solution arld insoluble lead carbonate, as well as lead dioxide, are separated at 13. The separated ammonium sulfate solution is then crystallized to recover solid ammonium sulfate at 14. The solid residues from the separation 13 are calcined at lS to produce 3~ impure lead oxide, oxygen and carbon dioxide. The formed carbon 1125~77 dioxide is drawn off at 16 and combined with ammonia 17 in tank 18 to form an ammonium carbonate solution~ The ammonium car-bonate solution is then added to the battery mud through line 19 at 12 to leach incoming battery mud. A carbon dioxide source 20 is used for start-up and make-up purposes to produce the ammonium carbonate solution. As previously mentioned, the ammonium carbonate desulfation may be carried out in two stages wherein fresh ammonium carbonate feed from the ammonia carbonation reaction at 18 is added to the second stage and the /~ ammonium carbonate solution used in the first stage is the un-expended ammonium carbonate solution recycled from the second stage.
After the calcination step 15, the impure lead monoxide and other impurities are subjected to an acetic acid leach at 21 to form a solution of lead acetate and an insoluble residue.
The lead acetate solution is separated from the solids at 22.
The solids, comprising an antimonial lead gangue is removed at 23 - for smelting. The lead acetate solution is treated with carbon dioxide at 24 to precipitate lead carbonate and form an acetic acid solution. After separation of the insoluble lead carbonate from the solution at 25, the lead carbonate is calcined by heat-- ing at 26 to form a pure PbO product at 27 and carbon dioxide.
A portion of the lead acetate solution may be used at this point to prepare other lead chemicals as well known in the art.
The acetic acid solution separated at 25 is then recycled to the acetic acid leach step via line 29 to leach incoming lead oxide at 21. Acetic acid solution 31, is used for make-up or start-up purposes.
The carbon dioxide from the calcination 26 is withdrawn 3O in line 32, compressed and recycled to carbonation step 24.
11~5477 Carbon dioxide source 34 is used for start-up and make-up purposes for the carbonation.
The invention will be more fully described with reference to the following Examples. All percentages given are by weight unless otherwise indlcated.
EXAMPLE I
Battery mud containing 71~ lead, 18% sulfate anion, 21% lead dioxide and minor amounts of antimony, iron and silica was fed to a desulfation reactor (primary reactor) with recycled ammonium carbonate from a second desulfation reactor and reacted to form a slurry containing about 30 to 40% solids. The battery mud was then leached (reacted) at about 20C. to 30C. for 30 minutes to convert 70 to 75% of the lead sulfate content to lead carbonate. The resulting slurry was thickened to a 66%
solids level by removal of a supernatant solution containing 17%
ammonium sulfate.
The solids slurry was then reacted with a fresh 6.5~
ammonium carbonate solution in countercurrent fashion in a secondary desulfation reactor at a 4 to 5:1 mole ratio of ammonium carbonate to lead sulfate to yield a lead carbonate slurry. The slurry was concentrated to a 66% solids level~
The resulting slurry was filtered and washed in a horizontal vacuum filter to form a 77% solids cake.
The filter cake was calcined at 550C. for about 1.5 hours in an inert or slightly oxidizing atmosphere to evaporate residual water and decompose the lead carbonate to lead monoxide and carbon dioxide. Fiber material associated with the battery mud was also decomposed along with lead dioxide to lead monoxide.
The calcined, desulfated battery mud containing lead monoxide in admixture with other solid impurities was combined with a 3.5 to 4.0% solution of acetic acid to form a 14 to 15%
solids slurry. The concentration of lead in the calcined feed is from about 75 to 90%. The so-formed mud was leached at 20 to 30C. for 1 hour resulting in a 3 to 6% solids slurry which was concentrated to a 40 to 45% slurry in a thickener, and then filtered in a horizontal vacuum filter to form a 66~ solids cake.
The overflow from the thickener is an 8 to 9% Pb-lead acetate ~O solution which was fed to a precipitation reactor. Gaseous carbon dioxide was bubbled into the solution at pressures of from 30 to 50 p.s.i.g. to precipitate lead carbonate. The slurry was then pressure filtered to a 90% solids lead carbonate cake. The filtrate, a 3.5 to 4~ acetic acid so]ution, was re-cycled to the leach reactor.
The lead carbonate cake was dried and decomposed to lead oxide and carbon dioxide at 600C. for 2 hours. The resulting substantially pure product had a total impurity concentration of around 1,100 ppm.
EXAMPLE II
The battery mud of Example I was desulfated as described ; in Example I.
The desulfated battery mud containing lead monoxide, lead oxide, lead dioxide, and lead carbonate in admixture with other solid impurities was combined with a 5.3 to 5.8% solution of acetic acid and a 30% hydrogen peroxide solution in a 1:1 stoichiometric ratio with the lead dioxide to form an 8 to 9 Pb-lead acetate solution. The mud was leached at 20 to 3~C.
for 1 hour. The resulting 2 to 3% solids slurry is concentrated 3~ to a 40 to 45% solids slurry in a thickener which is filtered to a 66% solids cake. This cake or gangue is collected and is suitable for conventional smelting operations. The filtrate was returned to the thickener.
The overflow from the thickener was an 8 to 9~ Pb lead acetate solution which was fed to a precipitation reactor.
Gaseous carbon dioxide is bubbled into the solution at pressures from 30 to 50 p.s.i.g. to precipitate lead carbonate. The slurry was then pressure filtered to a 90% solids lead carbonate cake.
The filtrate, a 2.5 to 3.5% acetic acid solution, was concentrated and recycled to the leach reactor.
The lead carbonate was then dried and decomposed to lead oxide and carbon dioxide at 600C. for 2 hours. The resulting substantially pure product had a total impurity concentration of around 630 ppm.
The invention being thus described, it will be obvious that the same may be varied in many ways, such variations are not to be regarded as a departure from the spirit and scope of the invention, and all such modifications are intended to be within the scope of the following claims.
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This invention is concerned with a process for preparing lead monoxide from impure lead sulfate bearing materials, particularly impure lead sulfate bearing materials such as recycled battery mud.
In the past, lead oxide has been produced by the oxidation of lead metal in a Barton Pot. The greatest single expense of the total manufacturing cost of producing lead monoxide is the cost of the lead metal. Such lead metal may be obtained by re-ducing reclaimed lead compounds such as lead sulfate, lead oxide and lead alloys from used battery plates. Not only is such ]ead oxide production costly but also involves the formation of noxious sulfur oxides as by-products which is environmentally unsatis-factory. Accordingly, there is substantial need for a process of producing pure lead monoxide from an inexpensive lead bearing material such as battery mud short of reducing lead compounds therein; refining the metal and oxidizing the so-formed lead metal.
In U.S. Patent No. 720,670 to A. C. J. Charlier, a method for producing white lead (lead carbonate) from litharge or lead oxide is provided comprising acidifying the oxide and contacting it with carbon dioxide gas under pressure.
In U.S. Patent No. 1,916,302 to L. P. Curtin, a process for recovering lead in the form of an acetate directly from lead ores, particularly lead sulfide containing galena ore is described.
The process comprises roasting the ore by the air-reduction pro-cess, to yield a product containing lead oxide, lead sulfate and basic lead sulfate, extracting the product with a solution of lead acetat~ to remove lead oxide values and extracting the residue from the lead acetate extraction with calcium or a~onium acetate to remove the lead sulfate values. The lead oxide dissolved in the lead acetate solution forms basic lead acetate .
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and may readily be precipitated by means of carbon dioxide as basic or normal lead carbonate. The lead carbonate may in turn be converted into lead monoxide by heating from 400C. to 475C.
Insoluble lead salts such as lead chromate or lead arsenate may be precipitated from the calcium or ammonium acetate solution after extraction.
In U.S. Patent No. 2,328,089 to J. J. Mulligan, a process is described for recovering soluble lead salts from raw materials such as insoluble lead compounds and impure lead bearing materials, e.g., lead sulfate, lead oxide, lead peroxide, spent litharge, old battery lead plates and lead battery mud or sediment. The soluble lead salts are suitable for the manufacture of lead com-pounds, such as lead arsenates, chromates, molybdates, tungstates, and acetates.
The aforementioned prior art process comprises first adding an aqueous solution of an alkali metal or ammonium carbonate or hydroxide to the raw material to convert the lead compound therein to an insoluhle lead compound. The insoluble residue from this addition is next treated with formic acid or acetic acid wherein ~Othe acetic acid preferably contains a reducing agent for lead peroxide contained in the residue, e.g., formic acid, nitrite salts, hydrogen peroxide, and hydrochloric acid. This treatment converts the insoluble lead compound to soluble acetate and for-mate salts which are in turn combined with appropriate reagents to make lead arsenate, lead chromate, and lead molybdate.
In U.S. Patent No. 3,883,348 to F. A. Acoveno and T. W.
Freudiger, a process for the treatment of lead bearing waste material such as battery mud is provided comprising agitating the waste material in a solution of ammonium carbonate to pro-3 0duce ammonium sulfate and lead carbonate, separating the solids from the liquid and heating the solids to decompose thelead carbonate contained therein to form lead monoxide.
The lead monoxide in combination with lead dioxide con-tained in the solids is used as furnace feed for final reduction to metallic lead. The carbon dioxide released during the carbonate decomposition stage is introduced to a condenser-absorber zone where ammonia and make-up carbon dioxide is added to produce ammonium carbonate.
The ammonium carbonate is then passed back or recycled to the leach solution to desulfate incoming waste material.
The present invention provides a multi-step hydro-metallurgical process for producing substantially pure lead monoxide from inexpensive lead bearing materials such as battery mud which involves the use of inexpensive and recyclable chemical reagents and physical treatments such as heating and solid/liquid separation.
The process of this invention employs a lead bearing material, particularly a lead sulfate bearing material such as battery mud, which may also contain lead oxides and other impurities.
An unexpected process for preparing lead oxide from lead bearing material has been discovered which comprises:
~ a) reacting said material with an ammonium carbonate solution to convert said lead sulfate to lead carbonate;
(b) decomposing substantially all of the lead carbonate to impure lead monoxide by heating at temperatures from about 400 to 650C., (c) reacting the impure lead monoxide with an effective amount of an acetic acid solution to convert said lead mon-oxide to a lead acetate solution;
llZ54~7 (d) separating said lead acetate solution from the insoluble impurities;
(e) contacting the lead acetate solution fro~ step (d) with carbon dioxide gas to form lead carbonate; and (f) decomposing the lead carbonate to produce lead monoxide.
- 4a -Any lead dioxide present in the lead bearing materïal may also be decomposed along with lead carbonate in step (b) of the process to produce additional lead monoxide. Alternatively, such lead dioxide may be treated with acetic acid in step (c) together with a reducing agent to simultaneously decompose the lead dioxide and form additional lead acetate.
In another embodiment of this invention, a continuous method for producing lead monoxide from a lead sulfate bearing material is provided wherein the by-products of reactions 1~ occurring in the above process are used to form the reagents used in the various steps of the process. More particularly, carbon dioxide formed as a by-product of the decomposition of lead carbonate in step (b~ can be separated and combined with ammonia to produce the ammonium carbonate solution used in step (a).
The carbon dioxide formed as a by-product of the decomposition of lead carbonate in step (ej can be recycled for use in step (d).
The acetic acid produced as a by-product in step (d) can be re-cycled for use in step (c).
In addltion, lead chemicals such as lead chromate, lead arsenate, and lead tungstate can be prepared by precipitation fr~m the lead acetate solution formed in step (c) with appro-priate reagents and separating the so-formed lead chemicals from the remaining solution.
Figure 1 is a flow diagram of the continuous method of this invention.
llZS477 The staxting material for the process of this invention is a lead bearing material, particularly a lead sulfate-bearing material such as battery mud. Such battery mud consists mainly of chemically reactive lead compounds such as lead sulfate, and amounts of lead dioxide, lead-antimony alloys and other complex lead bearing compounds. Such battery mud is produced by crush-ing the batteries and separating the battery parts, namely grid metal, plastics,and battery mud fines by well known separatory methods known in the art, from the mud.
~0 According to this invention, the lead bearing material is slurried in water and then leached with an ammonium carbonate solution wherein the lead sulfate contained therein is reacted and converted to insoluble lead carbonate and soluble ammonium sulfate according to the following reaction:
4 (NH4)2Co3 ~ PbC03 + (NH4)2S04 Unreacted materials such as lead dioxide remain undissolved in admixture with the insoluble lead carbonate in the ammonium sulfate solution.
Generally an aqueous solution Gf ammonium carbonate is employed containing from 1.5% to 12.5% ammonium carbonate and preferably about 6.5~. A lead battery mud containing from about 16-18 wt % of sulfate anion can he employed in the first step. Such mud is slurried with water to form a heterogeneous dispersion containing from about 10% to 60% by weight of mud and preferably about 35% by weight. The mud slurry and ammonium carbonate solution are then combined, preferably in counter-current fashion at a mole ratio of ammonium carbonate to lead sulfate in 3~ the mud slurry of from 1:1 to 1.25 at temperatures of from 25C.
llZ5477 to 35C., and preferably 30C. Reaction time may vary from 1 minute to 60 minutes but generally all reactions are com-pleted between 5 and 15 minutes.
After the reaction is substantially completed, the ammonium sulfate solution is separated from the lead carbonate and other insoluble materials by conventional solid/liquid separation techniques. The isolated ammonium sulfate solution may then be crystallized to recover solid ammonium sulfate.
Alternately and more preferably, the ammonium carbonate desulfation of battery mud may be carried out in two stages wherein fresh ammonium carbonate solution is added to the second stage and the ammonium carbonate solution used in the first stage is the unexpended ammonium carbonate solution from the second stage. In this embodiment, virgin battery mud is slurried in the first or primary stage with recovered ammonium carbonate solution from the secondary desulfation stage. The slurry is thickened by removal of supernatant ammonium sulfate solution.
The separated ammonium sulfate solution is then sent to an a~ ammonium sulfate crystallizer for recovery of solid ammonium sulfate. The thickened slurry is then reacted with fresh ammonium carbonate in a secondary stage to convert substantially all lead sulfate in the battery mud to lead carbonate and to form addi-tional ammonium sulfate. The lead carbonate and other insolubles in the form of a slurry is thickened and the thickened slurry is filtered and washed in a horizontal vacuum filter. The solution recovered from the thickener, containing both ammonium carbonate and ammonium sulfate is recycled to the first stage - desulfation above.
The lead carbonate and other insoluble material separated 1:125477 from the desulfation step are next calcined or heated at tempera-tures sufficient to decompose the lead carbonate to lead monoxide and carbon dioxide according to the following reaction:
PbC03 a - 3 PbO + Co2 Generally the temperatures required to decompose the lead carbonate are from 400C. to ~50C., and preferably 600C.
Preferably, the heating should be conducted in an inert atmosphere even though it may be conducted in a slightly oxidizing atmosphere.
Heating is conducted for between about 15 and 90 minutes to con-vert substantially all the lead carbonate to lead monoxide. Most usually, however, all decomposition is completed within 60 minutes. The carbon dioxide evolved may be separated from the lead monoxide and reacted with ammonia to form ammonium carbonate which may in turn be used as the ammonium carbonate leach for desulfation of the battery mud. This will be discussed in more detail in connection with Figure 1 depicting the continuous method of this invention.
Any lead dioxide contained in the insoluble residue after ammonium carbonate treatment may also be decomposed along with the lead carbonate to form additional lead monoxide and oxygen according to the following:
2PbO2 ~ 2PbO + 2 A portion of lead metal contained in the solids is also converted to lead monoxide. The lead monoxide product in ad- -mixture with undecomposed lead dioxide or lead carbonate and 3~ other insoluble materials is leached with an acetic acid solution (HAc). During this acetic acid leach step the lead monoxide reacts with acetic acid to form soluble lead acetate and/or basic lead acetate. While stoichiometric amounts of acetic acid to reactive lead may be employed, best results are achieved at mole ratios of 1:0.9 to 1.1.
PbO + HAc ~ PbAc2 + H2o lead (acetate) ~ or /O 2PbO + 2HAc ~ PbAc2-pb(oH)2 ,basic lead ~ acetate Any undecomposed lead carbonate is converted to soluble lead acetate by acetic acid during the reaction as follows:
PbCO3 + 2HAc - ~ PbAc2 + H20 + CO2 Alternatively to decompose and react lead dioxide in this step, a reducing agent such as hydrogen peroxide may be added with the acetic acid solution to form lead acetate as follows:
~O PbO2 + 2HAc + H2O2 -- ~ PbAc2 + 2H2 + 2 Generally, a 0.1-15 wt %, preferably a 0.5-5 wt % solu-tion of acetic acid is combined with the products of calcination ~ as a water slurry in stoichiometric ratios of 1:0.5 to 1.5 - acetate to reactive lead. The concentration of reactive leàd (lead carbonate, lead oxide and lead dioxide) in the calcined feed is not critical but for efficient operation the lead con-centration should be from 50% to 99% by weight. The solution is contacted with the slurry at a wide range of temperatures.
3D Increasing temperatures above about 15C. results in the _ g _ eoncomitant increase in reaction rate with preferred conditions being atmospheric pressure at temperatures from 25C. to 100C.
Reaction times between 5 and 60 minutes are necessary to com-plete the reaction.
The lead acetate solution formed by the reactions between the acetic acid and lead monoxide, undecomposed lead carbonate, if any, and lead dioxide, if any, plus reducing agent is separated from the insoluble residue containing minor amounts basic lead aeeta~e and antimonial lead gangue. The insoluble residue is then sent to a smelter to recover the antimony-lead values therefrom.
A portion of the separated lead aeetate solution may be used to prepare lead ehemieals such as lead chromate, lead tungstate, lead molybdate, lead arsenate and the like by re-action with appropriate reagents.
In order to prepare substantially pure lead monoxide from the lead acetate solution according to this invention, the lead acetate solution is next contacted with carbon dioxide gas under pressure to precipitate lead carbonate and acetic acid accordin~
to the following reaetion:
PbAc2 + CO2 ~ H2O ~ PbCO3 + 2HAc PbAc2-Pb(OH)2 + 2CO2 ~ ~ 2PbCO3 + 2HAc Generally, the carbon dioxide is bubbled into the lead acetate solution at pressures of from atmospheric to 250 p.s.i.g.
preferably from 20 to 100 p.s.i.g. at temperatures of from about 5C. to 95C., preferably from 40C. to 60C. The carbon 3O dioxide is added in an amount of from 0.5 to 1.2 moles per mole of lead in the lead acetate solution. Generally all conversion to lead carbonate is completed within 60 minutes.
The insoluble lead carbonate is next separated from the acetic acid solution and then calcined at temperatures of from 400 to 800C., preferably from 550 to 650C., in an inert or slightly oxidizing atmosphere for from one minute to reaction completion, to produce substantially pure lead monoxide and carbon dioxide. The vapors from the calcination are partially - condensed to yield an acetic acid solution which can be returned to the leach step. The non-condensed CO2 vapors can be com-pressed and recycled to the lead carbonate precipitation step in the continuous embodiment of this invention as will be shown in more detail below. The term substantially pure as used herein means the product contains less than 1~ impurities such as primary iron oxide and antimony oxide and preferably less than 0.1%
impurities.
Figure 1 shows a process flow diagram of one continuous method according to this invention wherein by-products of various reactions such as carbon dioxide from lead carbonate calcination, acetic acid from the lead acetate carbonation, and carbon dioxide from the lead carbonate calcination are recycled or used to prepare reagents used in the process.
A battery mud feed 11 containing lead sulfate, lead dioxide and other materials is leached with ammonium carbonate solution 12. The products, comprising an ammonium carbonate solution arld insoluble lead carbonate, as well as lead dioxide, are separated at 13. The separated ammonium sulfate solution is then crystallized to recover solid ammonium sulfate at 14. The solid residues from the separation 13 are calcined at lS to produce 3~ impure lead oxide, oxygen and carbon dioxide. The formed carbon 1125~77 dioxide is drawn off at 16 and combined with ammonia 17 in tank 18 to form an ammonium carbonate solution~ The ammonium car-bonate solution is then added to the battery mud through line 19 at 12 to leach incoming battery mud. A carbon dioxide source 20 is used for start-up and make-up purposes to produce the ammonium carbonate solution. As previously mentioned, the ammonium carbonate desulfation may be carried out in two stages wherein fresh ammonium carbonate feed from the ammonia carbonation reaction at 18 is added to the second stage and the /~ ammonium carbonate solution used in the first stage is the un-expended ammonium carbonate solution recycled from the second stage.
After the calcination step 15, the impure lead monoxide and other impurities are subjected to an acetic acid leach at 21 to form a solution of lead acetate and an insoluble residue.
The lead acetate solution is separated from the solids at 22.
The solids, comprising an antimonial lead gangue is removed at 23 - for smelting. The lead acetate solution is treated with carbon dioxide at 24 to precipitate lead carbonate and form an acetic acid solution. After separation of the insoluble lead carbonate from the solution at 25, the lead carbonate is calcined by heat-- ing at 26 to form a pure PbO product at 27 and carbon dioxide.
A portion of the lead acetate solution may be used at this point to prepare other lead chemicals as well known in the art.
The acetic acid solution separated at 25 is then recycled to the acetic acid leach step via line 29 to leach incoming lead oxide at 21. Acetic acid solution 31, is used for make-up or start-up purposes.
The carbon dioxide from the calcination 26 is withdrawn 3O in line 32, compressed and recycled to carbonation step 24.
11~5477 Carbon dioxide source 34 is used for start-up and make-up purposes for the carbonation.
The invention will be more fully described with reference to the following Examples. All percentages given are by weight unless otherwise indlcated.
EXAMPLE I
Battery mud containing 71~ lead, 18% sulfate anion, 21% lead dioxide and minor amounts of antimony, iron and silica was fed to a desulfation reactor (primary reactor) with recycled ammonium carbonate from a second desulfation reactor and reacted to form a slurry containing about 30 to 40% solids. The battery mud was then leached (reacted) at about 20C. to 30C. for 30 minutes to convert 70 to 75% of the lead sulfate content to lead carbonate. The resulting slurry was thickened to a 66%
solids level by removal of a supernatant solution containing 17%
ammonium sulfate.
The solids slurry was then reacted with a fresh 6.5~
ammonium carbonate solution in countercurrent fashion in a secondary desulfation reactor at a 4 to 5:1 mole ratio of ammonium carbonate to lead sulfate to yield a lead carbonate slurry. The slurry was concentrated to a 66% solids level~
The resulting slurry was filtered and washed in a horizontal vacuum filter to form a 77% solids cake.
The filter cake was calcined at 550C. for about 1.5 hours in an inert or slightly oxidizing atmosphere to evaporate residual water and decompose the lead carbonate to lead monoxide and carbon dioxide. Fiber material associated with the battery mud was also decomposed along with lead dioxide to lead monoxide.
The calcined, desulfated battery mud containing lead monoxide in admixture with other solid impurities was combined with a 3.5 to 4.0% solution of acetic acid to form a 14 to 15%
solids slurry. The concentration of lead in the calcined feed is from about 75 to 90%. The so-formed mud was leached at 20 to 30C. for 1 hour resulting in a 3 to 6% solids slurry which was concentrated to a 40 to 45% slurry in a thickener, and then filtered in a horizontal vacuum filter to form a 66~ solids cake.
The overflow from the thickener is an 8 to 9% Pb-lead acetate ~O solution which was fed to a precipitation reactor. Gaseous carbon dioxide was bubbled into the solution at pressures of from 30 to 50 p.s.i.g. to precipitate lead carbonate. The slurry was then pressure filtered to a 90% solids lead carbonate cake. The filtrate, a 3.5 to 4~ acetic acid so]ution, was re-cycled to the leach reactor.
The lead carbonate cake was dried and decomposed to lead oxide and carbon dioxide at 600C. for 2 hours. The resulting substantially pure product had a total impurity concentration of around 1,100 ppm.
EXAMPLE II
The battery mud of Example I was desulfated as described ; in Example I.
The desulfated battery mud containing lead monoxide, lead oxide, lead dioxide, and lead carbonate in admixture with other solid impurities was combined with a 5.3 to 5.8% solution of acetic acid and a 30% hydrogen peroxide solution in a 1:1 stoichiometric ratio with the lead dioxide to form an 8 to 9 Pb-lead acetate solution. The mud was leached at 20 to 3~C.
for 1 hour. The resulting 2 to 3% solids slurry is concentrated 3~ to a 40 to 45% solids slurry in a thickener which is filtered to a 66% solids cake. This cake or gangue is collected and is suitable for conventional smelting operations. The filtrate was returned to the thickener.
The overflow from the thickener was an 8 to 9~ Pb lead acetate solution which was fed to a precipitation reactor.
Gaseous carbon dioxide is bubbled into the solution at pressures from 30 to 50 p.s.i.g. to precipitate lead carbonate. The slurry was then pressure filtered to a 90% solids lead carbonate cake.
The filtrate, a 2.5 to 3.5% acetic acid solution, was concentrated and recycled to the leach reactor.
The lead carbonate was then dried and decomposed to lead oxide and carbon dioxide at 600C. for 2 hours. The resulting substantially pure product had a total impurity concentration of around 630 ppm.
The invention being thus described, it will be obvious that the same may be varied in many ways, such variations are not to be regarded as a departure from the spirit and scope of the invention, and all such modifications are intended to be within the scope of the following claims.
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Claims (15)
1. A process for producing lead monoxide from solid lead sulfate bearing material which comprises:
(a) reacting said material with an ammonium carbonate solution to convert said lead sulfate to lead carbonate;
(b) decomposing substantially all of the lead carbonate to impure lead monoxide by heating at temperatures from about 400° to 650°C., (c) reacting the impure lead monoxide with an effective amount of an acetic acid solution to convert said lead mon-oxide to a lead acetate solution;
(d) separating said lead acetate solution from the insoluble impurities;
(e) contacting the lead acetate solution from step (d) with carbon dioxide gas to form lead carbonate; and (f) decomposing the lead carbonate to produce lead monoxide.
(a) reacting said material with an ammonium carbonate solution to convert said lead sulfate to lead carbonate;
(b) decomposing substantially all of the lead carbonate to impure lead monoxide by heating at temperatures from about 400° to 650°C., (c) reacting the impure lead monoxide with an effective amount of an acetic acid solution to convert said lead mon-oxide to a lead acetate solution;
(d) separating said lead acetate solution from the insoluble impurities;
(e) contacting the lead acetate solution from step (d) with carbon dioxide gas to form lead carbonate; and (f) decomposing the lead carbonate to produce lead monoxide.
2. The process of claim 1 wherein said ammonium carbonate solution contains from 1.5% to 12.5% by weight of ammonium carbonate.
3. The process of claim 1 wherein said impure lead monoxide of step (b) contains undecomposed lead carbonate, said lead carbonate reacting with said acetic acid of step (c) to form lead acetate.
4. The process of claim 1 wherein the concentration of acetic acid in said acetic acid solution of step (c) is from 0.1 to 15%.
5. The process of claim 1 wherein the acetic acid solution of step (c) is added to the impure lead monoxide at a mole ratio of acetate to reactive lead of 1:0.9 to 1.1.
6. The process of claim 1 wherein said carbon dioxide gas is contacted with said lead acetate solution of step (e) at pressures of from atmospheric to 250 p.s.i.g.
7. A process for producing substantially pure lead monoxide from solid lead sulfate bearing battery mud, which comprises:
(a) reacting an aqueous dispersion of said battery mud with an ammonium carbonate solution to form lead carbonate and an ammonium sulfate solution;
(b) separating said ammonium sulfate solution from said lead carbonate;
(c) heating said lead carbonate to between about 400°
to 650° C. to decompose substantially all of said lead carbonate to impure lead monoxide;
(d) reacting said impure lead monoxide with acetic acid solution to convert said lead monoxide to a soluble lead acetate solution and an insoluble residue;
(e) separating said lead acetate solution from said insoluble residue;
(f) contacting said lead acetate solution from step (e) with carbon dioxide gas to form insoluble lead carbonate and acetic acid solution;
(g) separating said lead carbonate from said acetic acid solution; and (h) heating said lead carbonate to form substantially pure lead monoxide.
(a) reacting an aqueous dispersion of said battery mud with an ammonium carbonate solution to form lead carbonate and an ammonium sulfate solution;
(b) separating said ammonium sulfate solution from said lead carbonate;
(c) heating said lead carbonate to between about 400°
to 650° C. to decompose substantially all of said lead carbonate to impure lead monoxide;
(d) reacting said impure lead monoxide with acetic acid solution to convert said lead monoxide to a soluble lead acetate solution and an insoluble residue;
(e) separating said lead acetate solution from said insoluble residue;
(f) contacting said lead acetate solution from step (e) with carbon dioxide gas to form insoluble lead carbonate and acetic acid solution;
(g) separating said lead carbonate from said acetic acid solution; and (h) heating said lead carbonate to form substantially pure lead monoxide.
8. The process of claim 7 wherein step (a) is conducted at between about 25° to 60°C.
9. The process of claim 7 wherein said impure lead monoxide of step (d) is in the form of a water slurry containing from 10% to 25% of impure lead monoxide.
10. The process of claim 7 wherein the concentration of acetic acid in said acetic acid solution of step (d) is from 0.5% to 5%.
11. The process of claim 7 wherein said carbon dioxide gas is contacted with said lead acetate solution in step (f) at pressures of from atmospheric to 250 p.s.i.g.
12. The process of claim 7 wherein said lead carbonate in step (h) is heated to between from 550° to 650°.
13. A process for the continuous production of substan-tially pure lead monoxide from solid lead sulfate bearing material containing lead dioxide which comprising:
(a) reacting said material with an ammonium carbonate solution to form lead carbonate and an ammonium sulfate solution;
(b) separating the ammonium sulfate solution from the lead carbonate;
(c) heating said lead carbonate to between about 400°
to 650°C. to decompose substantially all of said lead carbonate to impure lead monoxide;
(d) reacting the lead monoxide with an effective amount of acetic acid solution to convert said lead mon-oxide to lead acetate solution and an insoluble residue;
(e) separating said insoluble residue from said lead acetate solution;
(f) contacting said lead acetate solution from step (e) with carbon dioxide gas to form lead carbonate and by-product acetic acid solution;
(g) separating said by-product acetic acid solution from said lead carbonate, said by-product acetic acid solution being used as the acetic acid reactant in step (d) and (h) decomposing said lead carbonate to form substan-tially pure lead monoxide and a second by-product carbon dioxide gas which is separated from said pure lead monoxide.
(a) reacting said material with an ammonium carbonate solution to form lead carbonate and an ammonium sulfate solution;
(b) separating the ammonium sulfate solution from the lead carbonate;
(c) heating said lead carbonate to between about 400°
to 650°C. to decompose substantially all of said lead carbonate to impure lead monoxide;
(d) reacting the lead monoxide with an effective amount of acetic acid solution to convert said lead mon-oxide to lead acetate solution and an insoluble residue;
(e) separating said insoluble residue from said lead acetate solution;
(f) contacting said lead acetate solution from step (e) with carbon dioxide gas to form lead carbonate and by-product acetic acid solution;
(g) separating said by-product acetic acid solution from said lead carbonate, said by-product acetic acid solution being used as the acetic acid reactant in step (d) and (h) decomposing said lead carbonate to form substan-tially pure lead monoxide and a second by-product carbon dioxide gas which is separated from said pure lead monoxide.
14. The process of claim 13 wherein steps (c) and (d) are performed by reacting the lead carbonate and lead dioxide with acetic acid and a reducing agent to form lead acetate.
15. A process for producing lead monoxide from solid lead sulfate bearing material, comprising:
(a) reacting said lead sulfate bearing material with an ammonium carbonate solution containing from 1.5% to 12.5% by weight of ammonium carbonate to convert said lead sulfate to lead carbonate;
(b) decomposing substantially all of the lead carbon-ate to impure lead monoxide by heating to between about 400° to 650°C.;
(c) reacting the impure lead monoxide with an acetic acid solution having a concentration of from 0.1% to 15%
acetic acid and further wherein said acetic acid is added to the impure lead monoxide at a mole ratio of acetate to reactive lead of 1:0.9 to 1.1;
(d) separating said lead acetate solution from the insoluble impurities;
(e) contacting the lead acetate solution from step (d) with carbon dioxide gas to form lead carbonate; and (f) decomposing the lead carbonate to produce lead monoxide.
(a) reacting said lead sulfate bearing material with an ammonium carbonate solution containing from 1.5% to 12.5% by weight of ammonium carbonate to convert said lead sulfate to lead carbonate;
(b) decomposing substantially all of the lead carbon-ate to impure lead monoxide by heating to between about 400° to 650°C.;
(c) reacting the impure lead monoxide with an acetic acid solution having a concentration of from 0.1% to 15%
acetic acid and further wherein said acetic acid is added to the impure lead monoxide at a mole ratio of acetate to reactive lead of 1:0.9 to 1.1;
(d) separating said lead acetate solution from the insoluble impurities;
(e) contacting the lead acetate solution from step (d) with carbon dioxide gas to form lead carbonate; and (f) decomposing the lead carbonate to produce lead monoxide.
Applications Claiming Priority (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| US95007878A | 1978-10-10 | 1978-10-10 | |
| US950,078 | 1978-10-10 |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CA1125477A true CA1125477A (en) | 1982-06-15 |
Family
ID=25489911
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CA337,238A Expired CA1125477A (en) | 1978-10-10 | 1979-10-09 | Production of lead monoxide from lead sulfate with acetic acid |
Country Status (9)
| Country | Link |
|---|---|
| BE (1) | BE879297A (en) |
| CA (1) | CA1125477A (en) |
| DE (1) | DE2941158A1 (en) |
| DK (1) | DK424479A (en) |
| FI (1) | FI793126A7 (en) |
| GB (1) | GB2033884B (en) |
| NL (1) | NL7907512A (en) |
| NO (1) | NO793218L (en) |
| SE (1) | SE7908361L (en) |
-
1979
- 1979-10-08 NO NO793218A patent/NO793218L/en unknown
- 1979-10-09 GB GB7935026A patent/GB2033884B/en not_active Expired
- 1979-10-09 SE SE7908361A patent/SE7908361L/en not_active Application Discontinuation
- 1979-10-09 FI FI793126A patent/FI793126A7/en not_active Application Discontinuation
- 1979-10-09 CA CA337,238A patent/CA1125477A/en not_active Expired
- 1979-10-09 BE BE0/197556A patent/BE879297A/en unknown
- 1979-10-09 DK DK424479A patent/DK424479A/en not_active Application Discontinuation
- 1979-10-10 DE DE19792941158 patent/DE2941158A1/en not_active Withdrawn
- 1979-10-10 NL NL7907512A patent/NL7907512A/en not_active Application Discontinuation
Also Published As
| Publication number | Publication date |
|---|---|
| DE2941158A1 (en) | 1980-04-24 |
| DK424479A (en) | 1980-04-11 |
| NL7907512A (en) | 1980-04-14 |
| FI793126A7 (en) | 1981-01-01 |
| SE7908361L (en) | 1980-04-11 |
| BE879297A (en) | 1980-04-09 |
| GB2033884B (en) | 1983-01-19 |
| NO793218L (en) | 1980-04-11 |
| GB2033884A (en) | 1980-05-29 |
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