CN109179486B - Preparation method of thallium chloride based on interface effect - Google Patents
Preparation method of thallium chloride based on interface effect Download PDFInfo
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- CN109179486B CN109179486B CN201811049605.4A CN201811049605A CN109179486B CN 109179486 B CN109179486 B CN 109179486B CN 201811049605 A CN201811049605 A CN 201811049605A CN 109179486 B CN109179486 B CN 109179486B
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- GBECUEIQVRDUKB-UHFFFAOYSA-M thallium monochloride Chemical compound [Tl]Cl GBECUEIQVRDUKB-UHFFFAOYSA-M 0.000 title claims abstract description 71
- 238000002360 preparation method Methods 0.000 title claims abstract description 38
- 230000000694 effects Effects 0.000 title description 2
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical class [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims abstract description 72
- VBIXEXWLHSRNKB-UHFFFAOYSA-N ammonium oxalate Chemical compound [NH4+].[NH4+].[O-]C(=O)C([O-])=O VBIXEXWLHSRNKB-UHFFFAOYSA-N 0.000 claims abstract description 39
- 239000003480 eluent Substances 0.000 claims abstract description 36
- 238000003756 stirring Methods 0.000 claims abstract description 32
- 239000013078 crystal Substances 0.000 claims abstract description 29
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical group Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims abstract description 28
- JGJLWPGRMCADHB-UHFFFAOYSA-N hypobromite Inorganic materials Br[O-] JGJLWPGRMCADHB-UHFFFAOYSA-N 0.000 claims abstract description 15
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 claims abstract description 11
- 238000010438 heat treatment Methods 0.000 claims abstract description 9
- 230000009471 action Effects 0.000 claims abstract description 5
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 claims description 158
- 229910052716 thallium Inorganic materials 0.000 claims description 91
- BKVIYDNLLOSFOA-UHFFFAOYSA-N thallium Chemical compound [Tl] BKVIYDNLLOSFOA-UHFFFAOYSA-N 0.000 claims description 87
- XEEYBQQBJWHFJM-UHFFFAOYSA-N iron Substances [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims description 53
- 239000000706 filtrate Substances 0.000 claims description 52
- 239000002253 acid Substances 0.000 claims description 50
- WCUXLLCKKVVCTQ-UHFFFAOYSA-M Potassium chloride Chemical group [Cl-].[K+] WCUXLLCKKVVCTQ-UHFFFAOYSA-M 0.000 claims description 42
- 239000001103 potassium chloride Substances 0.000 claims description 21
- 235000011164 potassium chloride Nutrition 0.000 claims description 21
- 239000000203 mixture Substances 0.000 claims description 18
- 238000000034 method Methods 0.000 claims description 12
- 239000000460 chlorine Substances 0.000 claims description 6
- 229910052742 iron Inorganic materials 0.000 claims description 6
- 238000001914 filtration Methods 0.000 claims description 5
- 238000001816 cooling Methods 0.000 claims description 3
- 238000001035 drying Methods 0.000 claims description 3
- 238000000227 grinding Methods 0.000 claims description 3
- 238000007254 oxidation reaction Methods 0.000 claims description 3
- 238000001179 sorption measurement Methods 0.000 claims description 3
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 claims description 2
- PXGOKWXKJXAPGV-UHFFFAOYSA-N Fluorine Chemical compound FF PXGOKWXKJXAPGV-UHFFFAOYSA-N 0.000 claims description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 2
- 229910052801 chlorine Inorganic materials 0.000 claims description 2
- 229910052731 fluorine Inorganic materials 0.000 claims description 2
- 239000011737 fluorine Substances 0.000 claims description 2
- 238000004519 manufacturing process Methods 0.000 claims description 2
- 230000003647 oxidation Effects 0.000 claims description 2
- 239000001301 oxygen Substances 0.000 claims description 2
- 229910052760 oxygen Inorganic materials 0.000 claims description 2
- -1 Hydrochloric acid modified activated carbon Chemical class 0.000 claims 3
- SZVJSHCCFOBDDC-UHFFFAOYSA-N ferrosoferric oxide Chemical compound O=[Fe]O[Fe]O[Fe]=O SZVJSHCCFOBDDC-UHFFFAOYSA-N 0.000 claims 2
- JEIPFZHSYJVQDO-UHFFFAOYSA-N iron(III) oxide Inorganic materials O=[Fe]O[Fe]=O JEIPFZHSYJVQDO-UHFFFAOYSA-N 0.000 claims 1
- 238000002386 leaching Methods 0.000 claims 1
- BOUDEKXATYHWHY-UHFFFAOYSA-K thallium(3+);trifluoride Chemical compound F[Tl](F)F BOUDEKXATYHWHY-UHFFFAOYSA-K 0.000 claims 1
- 238000000605 extraction Methods 0.000 abstract description 16
- 150000002736 metal compounds Chemical class 0.000 abstract description 2
- 230000000052 comparative effect Effects 0.000 description 26
- 239000007788 liquid Substances 0.000 description 20
- 239000002351 wastewater Substances 0.000 description 20
- 239000007787 solid Substances 0.000 description 19
- 238000006243 chemical reaction Methods 0.000 description 12
- 239000013067 intermediate product Substances 0.000 description 11
- 239000002994 raw material Substances 0.000 description 9
- 230000006872 improvement Effects 0.000 description 7
- 238000010298 pulverizing process Methods 0.000 description 7
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 description 6
- 229910017604 nitric acid Inorganic materials 0.000 description 6
- 150000002500 ions Chemical class 0.000 description 5
- 239000002245 particle Substances 0.000 description 5
- CWYNVVGOOAEACU-UHFFFAOYSA-N Fe2+ Chemical compound [Fe+2] CWYNVVGOOAEACU-UHFFFAOYSA-N 0.000 description 4
- 229910004298 SiO 2 Inorganic materials 0.000 description 4
- 239000012141 concentrate Substances 0.000 description 4
- JQJCSZOEVBFDKO-UHFFFAOYSA-N lead zinc Chemical compound [Zn].[Pb] JQJCSZOEVBFDKO-UHFFFAOYSA-N 0.000 description 4
- 230000009257 reactivity Effects 0.000 description 4
- 239000007790 solid phase Substances 0.000 description 4
- 238000003723 Smelting Methods 0.000 description 3
- 239000003153 chemical reaction reagent Substances 0.000 description 3
- 239000000413 hydrolysate Substances 0.000 description 3
- 239000007791 liquid phase Substances 0.000 description 3
- 239000012071 phase Substances 0.000 description 3
- 230000008569 process Effects 0.000 description 3
- 238000000746 purification Methods 0.000 description 3
- 239000002699 waste material Substances 0.000 description 3
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N Iron oxide Chemical compound [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 description 2
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 2
- 238000010406 interfacial reaction Methods 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 239000011159 matrix material Substances 0.000 description 2
- 238000001556 precipitation Methods 0.000 description 2
- 238000006479 redox reaction Methods 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- 239000002893 slag Substances 0.000 description 2
- CMJCEVKJYRZMIA-UHFFFAOYSA-M thallium(i) iodide Chemical compound [Tl]I CMJCEVKJYRZMIA-UHFFFAOYSA-M 0.000 description 2
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 1
- KRHYYFGTRYWZRS-UHFFFAOYSA-M Fluoride anion Chemical compound [F-] KRHYYFGTRYWZRS-UHFFFAOYSA-M 0.000 description 1
- 235000011941 Tilia x europaea Nutrition 0.000 description 1
- 239000013064 chemical raw material Substances 0.000 description 1
- 150000001805 chlorine compounds Chemical class 0.000 description 1
- 238000000975 co-precipitation Methods 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000001514 detection method Methods 0.000 description 1
- 238000010494 dissociation reaction Methods 0.000 description 1
- 230000005593 dissociations Effects 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- XMBWDFGMSWQBCA-UHFFFAOYSA-N hydrogen iodide Chemical compound I XMBWDFGMSWQBCA-UHFFFAOYSA-N 0.000 description 1
- 230000007062 hydrolysis Effects 0.000 description 1
- 238000006460 hydrolysis reaction Methods 0.000 description 1
- 238000003384 imaging method Methods 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 229910052500 inorganic mineral Inorganic materials 0.000 description 1
- 239000000543 intermediate Substances 0.000 description 1
- 230000016507 interphase Effects 0.000 description 1
- 239000004571 lime Substances 0.000 description 1
- 235000010755 mineral Nutrition 0.000 description 1
- 239000011707 mineral Substances 0.000 description 1
- 230000005501 phase interface Effects 0.000 description 1
- 230000035484 reaction time Effects 0.000 description 1
- 238000006722 reduction reaction Methods 0.000 description 1
- 239000013049 sediment Substances 0.000 description 1
- 239000004065 semiconductor Substances 0.000 description 1
- 239000011780 sodium chloride Substances 0.000 description 1
- 230000002269 spontaneous effect Effects 0.000 description 1
- 230000009466 transformation Effects 0.000 description 1
Classifications
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- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01G—COMPOUNDS CONTAINING METALS NOT COVERED BY SUBCLASSES C01D OR C01F
- C01G15/00—Compounds of gallium, indium or thallium
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- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Inorganic Chemistry (AREA)
- Removal Of Specific Substances (AREA)
- Pharmaceuticals Containing Other Organic And Inorganic Compounds (AREA)
Abstract
本发明公开了一种基于界面作用的氯化亚铊的制备方法,属于金属化合物制备技术领域,该制备方法是以硫酸灰渣、稀酸和含有F‑的稀酸为原料提取出Tl+,溴水再将Tl+氧化成Tl3+;盐酸改性的活性炭吸附Tl3+,草酸铵溶液从盐酸改性的活性炭中还原并洗脱出Tl+,即得Tl+洗脱液;向Tl+洗脱液中加入氯化物,搅拌加热使TlCl晶体析出。本发明制备方法能缩短提取时间和制备出更纯的氯化亚铊。The invention discloses a preparation method of thallium chloride based on interface action, which belongs to the technical field of metal compound preparation . Bromine water oxidizes Tl + into Tl 3+ again; the activated carbon modified with hydrochloric acid adsorbs Tl 3+ , and the ammonium oxalate solution is reduced from the activated carbon modified with hydrochloric acid and eluted out Tl + , that is, Tl + eluent is obtained; + Chloride was added to the eluent, and the TlCl crystals were precipitated by stirring and heating. The preparation method of the invention can shorten the extraction time and prepare purer thallium chloride.
Description
技术领域technical field
本发明属于金属化合物制备技术领域,尤其涉及一种基于界面作用的氯化亚铊的制备方法。The invention belongs to the technical field of metal compound preparation, in particular to a preparation method of thallium chloride based on interface action.
背景技术Background technique
氯化亚铊晶体的宽价带(4ev)约为一般绝缘晶体(1-2ev)的2-4倍,而带隙(3ev)仅为一般绝缘晶体(约10ev)的1/3,氯化亚铊晶体是一种很好的半导体材料,广泛用于安全检测和成像领域。氯化亚铊也是制备铊试剂的化工原料,以氯化亚铊作原料可以制备各种纯度较高的铊试剂。The broad valence band (4ev) of thallium chloride crystals is about 2-4 times that of general insulating crystals (1-2ev), while the band gap (3ev) is only 1/3 of that of general insulating crystals (about 10ev). Thallium sub-crystal is a good semiconductor material, which is widely used in the fields of security detection and imaging. Thallium chloride is also a chemical raw material for the preparation of thallium reagents, and various thallium reagents with high purity can be prepared by using thallium chloride as a raw material.
中国发明专利“一种以铅锌矿冶炼废水作原料制备氯化亚铊的方法”(申请号为201410023981.1,申请日为2014年1月18日):其以铅锌矿废渣和冶炼废水按1:500比例搅拌,并加石灰沉淀吸附共沉淀制得底泥,从废水提取铊从而制备氯化亚铊,但存在一些不足:铅锌矿是多金属矿产,铅锌矿废渣及冶炼废水中重金属含量均高,所得氯化亚铊杂质多,提纯复杂。Chinese invention patent "a method for preparing thallium chloride with lead-zinc ore smelting wastewater as raw material" (application number is 201410023981.1, application date is January 18, 2014): it uses lead-zinc ore slag and smelting wastewater according to 1 : 500 ratio stirring, and adding lime precipitation, adsorption and co-precipitation to obtain sediment, extract thallium from wastewater to prepare thallium chloride, but there are some shortcomings: lead-zinc ore is a polymetallic mineral, and heavy metals in lead-zinc ore residue and smelting wastewater The content is high, the obtained thallium chloride has many impurities, and the purification is complicated.
因此,有必要设计出一种高效率的氯化亚铊的制备方法,其能缩短提取时间,又能制备更纯的氯化亚铊。Therefore, it is necessary to design a high-efficiency preparation method of thallium chloride, which can shorten the extraction time and can prepare purer thallium chloride.
发明内容SUMMARY OF THE INVENTION
本发明目的在于克服现有技术存在的不足,而提供一种基于界面作用的氯化亚铊的制备方法,其能缩短提取时间和制备出更纯的氯化亚铊。The purpose of the present invention is to overcome the deficiencies of the prior art, and to provide a preparation method of thallium chloride based on interfacial action, which can shorten the extraction time and prepare purer thallium chloride.
为实现上述目的,本发明采取的技术方案为:一种基于界面作用的氯化亚铊的制备方法,其先以硫酸灰渣、稀酸和含有F-的稀酸为原料提取出Tl+,溴水再将Tl+氧化成Tl3+;盐酸改性的活性炭吸附Tl3+,草酸铵溶液从盐酸改性的活性炭中还原并洗脱出Tl+,即得Tl+洗脱液;向Tl+洗脱液中加入氯化物,搅拌加热使TlCl晶体析出;所述硫酸灰渣包含Fe2O3、Fe3O4、TlF、TlF3、Tl2F4、Tl4F6、Tl3F5和Tl3F7,所述稀酸的pH值为3-4;其中,Tl表示铊,F表示为氟,Fe表示铁,O表示氧,Cl表示氯。In order to achieve the above object, the technical solution adopted in the present invention is: a preparation method of thallium chloride based on interfacial action, which first uses sulfuric acid ash, dilute acid and dilute acid containing F as raw materials to extract Tl + , Bromine water oxidizes Tl + into Tl 3+ again; the activated carbon modified with hydrochloric acid adsorbs Tl 3+ , and the ammonium oxalate solution is reduced from the activated carbon modified with hydrochloric acid and eluted out Tl + , that is, Tl + eluent is obtained; + Chloride is added to the eluent, stirred and heated to precipitate TlCl crystals; the sulfuric acid ash residue includes Fe 2 O 3 , Fe 3 O 4 , TlF, TlF 3 , Tl 2 F 4 , Tl 4 F 6 , Tl 3 F 5 and Tl 3 F 7 , the pH of the dilute acid is 3-4; wherein, Tl represents thallium, F represents fluorine, Fe represents iron, O represents oxygen, and Cl represents chlorine.
作为上述技术方案的改进,该制备方法依次包括以下步骤:As the improvement of above-mentioned technical scheme, this preparation method comprises the following steps successively:
S1)将硫酸灰渣研磨粉碎,向硫酸灰渣中加入稀酸,搅拌振荡4-6h,过滤即得滤液Ⅰ和滤渣Ⅰ;S1) grinding and pulverizing the sulfuric acid ash residue, adding dilute acid to the sulfuric acid ash residue, stirring and shaking for 4-6h, and filtering to obtain filtrate I and filter residue I;
S2)向所述滤渣Ⅰ中继续加入稀酸,重复步骤S1)的操作,重复的次数至少为3次,即得滤液Ⅱ和滤渣Ⅱ;S2) continue to add dilute acid to described filter residue I, repeat the operation of step S1), and the number of repetitions is at least 3 times to obtain filtrate II and filter residue II;
S3)向所述滤渣Ⅱ中含有F-的稀酸,搅拌静置后过滤,即得滤液Ш;S3) in described filter residue II, contain the dilute acid of F- , after stirring and standing, filter, obtain filtrate Ш;
S4)合并所述滤液Ⅰ、所述滤液Ⅱ和所述滤液Ш,即得铊提取液Ⅰ;S4) merging the filtrate I, the filtrate II and the filtrate Ш to obtain the thallium extract I;
S5)向所述铊提取液Ⅰ中滴加溴水至微黄色,加入盐酸改性的活性碳,搅拌30-60min,过滤后即得活性炭混合物;S5) dropwise add bromine water to the thallium extract I until slightly yellow, add hydrochloric acid-modified activated carbon, stir for 30-60min, and filter to obtain an activated carbon mixture;
S6)用加热的草酸铵溶液分多次淋洗所述活性碳混合物,收集洗脱液即得Tl+洗脱液;S6) wash described activated carbon mixture with heated ammonium oxalate solution for several times, collect eluent and obtain T1 + eluent;
S7)向所述Tl+洗脱液中加入氯化物,搅拌、加热浓缩,即得铊提取液Ⅱ;对所述铊提取液Ⅱ进行冷却、干燥,即得TlCl晶体。S7) adding chloride to the Tl + eluent, stirring, heating and concentrating to obtain thallium extract II; cooling and drying the thallium extract II to obtain TlCl crystals.
在步骤S1),向硫酸灰渣中加入pH值为3.0-4.0的稀酸(如HCl、HNO3和H2SO4),搅拌振荡,铁氧化物发生水解:In step S1), add dilute acid (such as HCl, HNO 3 and H 2 SO 4 ) with a pH value of 3.0-4.0 to the sulfuric acid ash, stir and shake, and the iron oxide is hydrolyzed:
3Fe2O3+2H2O+7H+→Fe(OH)2++5Fe(OH)2 + (1)3Fe 2 O 3 +2H 2 O+7H + →Fe(OH) 2+ +5Fe(OH) 2 + (1)
2Fe3O4+H2O+7H+→2Fe(OH)++2Fe(OH)2 0+Fe(OH)2++Fe(OH)2 + (2)2Fe 3 O 4 +H 2 O+7H + →2Fe(OH) + +2Fe(OH) 2 0 +Fe(OH) 2+ +Fe(OH) 2 + (2)
TlF、TlF3及其中间产物是一个非均相体系,TlF易溶(80g/100g H2O),TlF3难溶(易潮解/H2O),中间产物Tl2F4(Tl+Tl3+F4)、Tl4F6(Tl3 +Tl3+F6)、Tl3F5(Tl2 +Tl3+F5)和Tl3F7(Tl+Tl2 3+F7)含非配位的Tl+和Tl3+,存在自发的热力学过程(Tl3+/Tl+=1.25V,Fe3+/Fe2+=0.77V);因此,在硫酸灰渣-溶液这个固-液界面上,包含了溶液(液相)-水解产物(胶体相)、中间产物(固相)-水解产物(胶体相)以及溶液(液相)-TlF和TlF3(固相)等多相界面。相间界面区因其特殊的物化和生化性质常具有特别的界面反应活性,其物质传输、转化往往是整个反应的关键步骤。TlF, TlF 3 and their intermediate products are a heterogeneous system, TlF is easily soluble (80g/100g H 2 O), TlF 3 is insoluble (easy deliquescence/H 2 O), and the intermediate product Tl 2 F 4 (Tl + Tl 3 + F4 ), Tl4F6 ( Tl3 + Tl3 + F6), Tl3F5 (Tl2 + Tl3 + F5 ) and Tl3F7 (Tl + Tl23 + F7 ) With uncoordinated Tl + and Tl 3+ , there is a spontaneous thermodynamic process (Tl 3+ /Tl + =1.25V, Fe 3+ /Fe 2+ =0.77V); - On the liquid interface, including solution (liquid phase)-hydrolysate (colloidal phase), intermediate product (solid phase)-hydrolysate (colloidal phase) and solution (liquid phase)-TlF and TlF 3 (solid phase) phase interface. The interphase interface region often has special interface reactivity due to its special physicochemical and biochemical properties, and its material transport and transformation are often the key steps in the entire reaction.
在步骤S2)中,至少重复S1)3次,优选地重复S1)3次,强化界面过程,进一步提取硫酸灰渣的铊;此时,在溶液(液相)-水解产物(胶体相)界面,Fe2+和Fe3+进一步水解:In step S2), repeat S1) at least 3 times, preferably repeat S1) 3 times, strengthen the interface process, and further extract the thallium of the sulfated ash; , Fe 2+ and Fe 3+ are further hydrolyzed:
Fe(OH)++OH-→Fe(OH)2 0 (3)Fe(OH) + +OH - →Fe(OH) 2 0 (3)
Fe(OH)2++OH-→Fe(OH)2 + (4);Fe(OH) 2+ +OH - →Fe(OH) 2 + (4);
在中间产物(固相)-水解产物(胶体相)界面:一方面,Tl3+/Tl+和Fe3+/Fe2+电对可自发地发生氧化还原反应;另方面,Fe(OH)2 0的两个OH-反向拉伸使其荷电为零,Fe2+的电子云明显向两边偏移,反应活性显著增强,与中间产物快速发生氧化反应:At the interface of intermediate product (solid phase)-hydrolysate (colloidal phase): on the one hand, Tl 3+ /Tl + and Fe 3+ /Fe 2+ pairs can spontaneously undergo redox reactions; on the other hand, Fe(OH) The reverse stretching of the two OH- of 2 0 makes the charge zero, the electron cloud of Fe 2+ is obviously shifted to both sides, the reactivity is significantly enhanced, and the oxidation reaction with the intermediate product occurs rapidly:
Tl2F4(+2e)+2Fe(OH)2 0→2TlF2 -+2Fe(OH)2 + (5)Tl 2 F 4 (+2e)+2Fe(OH) 2 0 →2TlF 2 - +2Fe(OH) 2 + (5)
Tl4F6(+2e)+2Fe(OH)2 0→2TlF2 -+2TlF0+2Fe(OH)2 + (6)Tl 4 F 6 (+2e)+2Fe(OH) 2 0 →2TlF 2 - +2TlF 0 +2Fe(OH) 2 + (6)
Tl3F5(+2e)+2Fe(OH)2 0→2TlF2 -+TlF3 2-+2Fe(OH)2 + (7)Tl 3 F 5 (+2e)+2Fe(OH) 2 0 →2TlF 2 - +TlF 3 2- +2Fe(OH) 2 + (7)
Tl3F7(+4e)+4Fe(OH)2 0→2TlF3 2-+TlF0+4Fe(OH)2 + (8);Tl 3 F 7 (+4e)+4Fe(OH) 2 0 →2TlF 3 2- +TlF 0 +4Fe(OH) 2 + (8);
(5)-(8)形成的Fe(OH)2 +又可继续与中间产物发生还原反应,使Fe(OH)2 0再生(中间产物部分Tl+被氧化):The Fe(OH) 2 + formed by (5)-(8) can continue to undergo reduction reaction with the intermediate product to regenerate Fe(OH) 2 0 (the intermediate product part Tl + is oxidized):
Tl2F4(-2e)+2Fe(OH)2 +→2TlF3 0+2Fe(OH)2 0 (9)Tl 2 F 4 (-2e)+2Fe(OH) 2 + →2TlF 3 0 +2Fe(OH) 2 0 (9)
Tl4F6(-2e)+2Fe(OH)2 +→2TlF3 0+2Tl++2Fe(OH)2 0 (10)Tl 4 F 6 (-2e)+2Fe(OH) 2 + →2TlF 3 0 +2Tl + +2Fe(OH) 2 0 (10)
Tl3F5(-2e)+2Fe(OH)2 +→2TlF2 ++TlF0+2Fe(OH)2 0 (11)Tl 3 F 5 (-2e)+2Fe(OH) 2 + →2TlF 2 + +TlF 0 +2Fe(OH) 2 0 (11)
Tl3F7(-2e)+2Fe(OH)2 +→2TlF3 0+TlF0+2Fe(OH)2 0 (12)Tl 3 F 7 (-2e)+2Fe(OH) 2 + →2TlF 3 0 +TlF 0 +2Fe(OH) 2 0 (12)
TlF3 0对湿气敏感:TlF3 0+H2O→Tl(OH)3+HF (13);TlF 3 0 is sensitive to moisture: TlF 3 0 +H 2 O→Tl(OH) 3 +HF (13);
(9)-(13)形成的Fe(OH)2 0又继续与中间产物发生上述(5)-(8)的系列反应,之后又是(9)-(13)的系列反应,如此延续,直至灰渣的中间产物以氟-铊配离子的形式全部溶解。The Fe(OH) 2 O formed by ( 9 )-(13) continues the series reaction of (5)-(8) above with the intermediate product, and then the series reaction of (9)-(13), which continues like this, Until the intermediate product of the ash residue is completely dissolved in the form of fluorine-thallium complex ions.
氟-铊配离子易解离:Fluorine-thallium complex ions are easily dissociated:
TlF0→Tl++F- (14)TlF 0 →Tl + +F - (14)
TlF2 -→Tl++2F- (15)TlF 2 - → Tl + +2F - (15)
TlF3 2-→Tl++3F- (16)TlF 3 2- →Tl + +3F - (16)
TlF2 +→Tl3++2F- (17);TlF 2 + →Tl 3+ +2F - (17);
解离后的Tl3+水解吸附溶液中的Tl+:The dissociated Tl 3+ hydrolysis adsorption solution of Tl + :
Tl3++OH-→Tl(OH)3 (18)Tl 3+ +OH - →Tl(OH) 3 (18)
Tl(OH)3+Tl+→Tl(OH)3-Tl+ (19);Tl(OH) 3 +Tl + →Tl(OH) 3 -Tl + (19);
从反应(13)、(18)和(19)可知,溶液中的Tl+被Tl(OH)3吸附,从反应(5)-(8)、(11)-(12)和(14)-(17)可知,大量F-进入溶液;于是,在溶液(液相)-TlF和TlF3(固相)界面,TlF和TlF3可以氟-铊配离子的形式溶解:From reactions (13), (18) and (19), it is known that Tl + in solution is adsorbed by Tl(OH) 3 , from reactions (5)-(8), (11)-(12) and (14)- (17) It can be seen that a large amount of F- enters the solution; then, at the interface of solution (liquid phase)-TlF and TlF 3 (solid phase), TlF and TlF 3 can be dissolved in the form of fluorine-thallium complex ions:
3TlF+6F-→TlF2 -+TlF3 2-+TlF4 3- (20)3TlF+6F - →TlF 2 - +TlF 3 2- +TlF 4 3- (20)
TlF3+F-→TlF4 -(K=1.3×10-2) (21);TlF 3 +F − →TlF 4 − (K=1.3×10 −2 ) (21);
形成的氟-铊配离子再次解离:The formed fluorine-thallium complex ion dissociates again:
TlF4 3-→Tl3++4F- (22)TlF 4 3- → Tl 3+ +4F- (22)
TlF2 -和TlF3 2-的解离见(15)和(16);The dissociation of TlF 2 - and TlF 3 2- see (15) and (16);
至此,非均相体系的TlF、TlF3及其中间产物均可通过界面反应进入溶液。So far, TlF, TlF 3 and their intermediates in the heterogeneous system can all enter the solution through the interfacial reaction.
之前申请的中国发明专利“一种碘化亚铊的制备方法”(申请号为201810264009.1,申请日为2018年3月28日),以硫酸灰渣、硫酸废水和碘化物为原料进行制备,当时尚未发现中间产物,提取方案主要针对硫酸灰渣含TlF和TlF3而设计,通过含F-的强酸溶解和碱液沉淀灰渣的Tl+;后期研究发现硫酸灰渣中存在TlF-TlF3和TlCl-TlCl3两种非均相体系,由于两种非均相体系在强酸溶解时均参与氧化还原反应,所以产量相对较高;但强酸溶解时,铁氧化物以Fe3+和Fe2+溶解,其中Fe2+的反应活性不及Fe(OH)2 0,因此,提取时间较长。这点与芬顿反应中Fe(OH)2 0与H2O2的反应很相似,芬顿反应中,当pH<3时,亚铁物种主要以Fe2+存在:The previously applied Chinese invention patent "a preparation method of thallium iodide" (application number is 201810264009.1, application date is March 28, 2018), prepared with sulfuric ash, sulfuric acid wastewater and iodide as raw materials, at that time No intermediate product has been found, and the extraction scheme is mainly designed for the sulfuric ash containing TlF and TlF 3 , through the strong acid containing F - dissolving and lye precipitation of the ash Tl + ; later research found that there are TlF-TlF 3 and TlF in the sulfuric ash. Two heterogeneous systems, TlCl - TlCl 3 , have relatively high yields because both of the two heterogeneous systems participate in the redox reaction when the strong acid dissolves; Dissolved, in which Fe 2+ is less reactive than Fe(OH) 2 0 , so the extraction time is longer. This is very similar to the reaction of Fe(OH) 2 0 with H 2 O 2 in the Fenton reaction. In the Fenton reaction, when pH<3, the ferrous species mainly exist as Fe 2+ :
Fe2++H2O2→Fe3++OH-+.OH (23)Fe 2+ +H 2 O 2 →Fe 3+ +OH - + . OH (23)
Fe3++H2O2→Fe2++H++HO2 . (24)Fe 3+ +H 2 O 2 →Fe 2+ +H + +HO 2 . (24)
Fe3++HO2 .→Fe2++O2+H+ (25);Fe 3+ +HO 2 . →Fe 2+ +O 2 +H + (25);
当pH为3-4时,亚铁物种的水解形态为Fe(OH)+和Fe(OH)2 0,其中Fe(OH)2 0的反应活性是Fe2+的近10倍,使得.OH和Fe(OH)2 +可大量生成,体系的氧化能力显著增强(吕来和胡春,2017),与本发明反应(5)-(12)异曲同工;因此,本发明实质是利用:1)TlF-TlF3非均相体系的中间产物与Fe(OH)2 0的类芬顿效应,2)TlF-TlF3非均相体系的TlF和TlF3的界面反应提取硫酸灰渣的铊,反应时间可明显缩短。由于TlF溶解度大,在灰渣风化过程易进入环境造成污染,本发明力图借助类芬顿反应最大限度地提取TlF-TlF3非均相体系中的铊,防止其污染环境。When the pH is 3-4, the hydrolyzed forms of ferrous species are Fe(OH) + and Fe(OH) 2 0 , of which Fe(OH) 2 0 is nearly 10 times more reactive than Fe 2+ , making .OH and Fe(OH) 2 + can be generated in large quantities, and the oxidation capacity of the system is significantly enhanced (Lv Lai and Hu Chun, 2017), which is similar to the reactions (5)-(12) of the present invention; therefore, the essence of the present invention is to utilize: 1) Fenton-like effect between intermediate products of TlF-TlF 3 heterogeneous system and Fe(OH) 2 0 , 2) Interfacial reaction of TlF and TlF 3 of TlF-TlF 3 heterogeneous system to extract thallium from sulfated ash, reaction time can be significantly shortened. Due to the high solubility of TlF, it is easy to enter the environment during the ash weathering process and cause pollution. The present invention tries to extract thallium in the TlF-TlF 3 heterogeneous system to the maximum extent by means of the Fenton-like reaction to prevent it from polluting the environment.
在步骤S3)中,向滤渣Ⅱ中加入含氟离子的稀酸,解吸滤渣Ⅱ中的铊,过滤,保留滤液Ш:In step S3), add dilute acid containing fluoride ion to filter residue II, desorb thallium in filter residue II, filter, and retain filtrate Ш:
Tl++F-→TlF0(ΔGf=-311.8kJmol-1) (26)Tl + +F - →TlF 0 (ΔGf=-311.8kJmol -1 ) (26)
TlF0(lgK=0.1)→Tl++F- (27)。TlF 0 (lgK=0.1)→Tl + +F − (27).
在步骤S5)中,向铊提取液Ⅰ中滴加溴水至微黄色,把Tl+全部氧化为Tl3+;加入盐酸改性的活性碳,富集铊提取液Ⅰ的铊,使之与复杂基体分离而提纯:In step S5), bromine water is added dropwise to the thallium extraction solution I until it is slightly yellow, and all Tl + is oxidized to Tl 3+ ; activated carbon modified with hydrochloric acid is added to enrich the thallium of the thallium extraction solution I to make it with Complex matrix separation and purification:
Tl++Br2→Tl3++2Br- (28)Tl + +Br 2 →Tl 3+ +2Br - (28)
Tl3++4Cl-→TlCl4 - (29);Tl 3+ +4Cl - → TlCl 4 - (29);
盐酸改性的活性炭是通过以下方法进行制备的:活性碳用前需经105℃烘箱烘2h,1.5-3.5mol/L的盐酸淋洗10次以上。The activated carbon modified with hydrochloric acid is prepared by the following method: before the activated carbon is used, it needs to be dried in a 105 ℃ oven for 2 hours, and rinsed with 1.5-3.5 mol/L hydrochloric acid for more than 10 times.
在步骤S5)中,向铊提取液Ⅰ中滴加溴水至微黄色,把Tl+全部氧化为Tl3+;加入盐酸改性的活性碳,富集铊提取液Ⅰ的铊,使之与复杂基体分离而提纯:In step S5), bromine water is added dropwise to the thallium extraction solution I until it is slightly yellow, and all Tl + is oxidized to Tl 3+ ; activated carbon modified with hydrochloric acid is added to enrich the thallium of the thallium extraction solution I to make it with Complex matrix separation and purification:
Tl++Br2→Tl3++2Br- (30)Tl + +Br 2 →Tl 3+ +2Br - (30)
Tl3++4Cl-→TlCl4 - (31)。Tl 3+ +4Cl - → TlCl 4 - (31).
在步骤S6)中,用热草酸铵溶液反复淋洗活性碳混合物,洗脱活性碳混合物中铊:In step S6), the activated carbon mixture is repeatedly rinsed with hot ammonium oxalate solution to elute the thallium in the activated carbon mixture:
(NH4)2C2O4+TlCl4 -→2(NH4)Cl+2CO2↑+TlCl2 - (32)(NH 4 ) 2 C 2 O 4 +TlCl 4 - →2(NH 4 )Cl+2CO 2 ↑+TlCl 2 - (32)
在步骤S7)中,向铊提取液Ⅱ中加入氯化物(如NaCl和KCl):In step S7), add chlorides (such as NaCl and KCl) to the thallium extract II:
Tl++Cl-→TlCl (33)。Tl + +Cl - → TlCl (33).
本发明是先提取硫酸灰渣发生类芬顿反应产生的Tl+,以及硫酸灰渣中Tl+,再用溴水氧化成Tl3+,盐酸改性的活性炭吸附Tl3+,草酸铵溶液洗脱并将Tl3+还原成Tl+,制备出更纯的TlCl。In the present invention, the Tl + produced by the Fenton-like reaction of the sulfuric acid ash is first extracted, and the Tl + in the sulfuric acid ash is oxidized to Tl 3+ with bromine water, the activated carbon modified with hydrochloric acid adsorbs the Tl 3+ , and the ammonium oxalate solution washes the Tl 3+ . Detach and reduce Tl 3+ to Tl + to produce purer TlCl.
作为上述技术方案的进一步改进,在步骤S1)中,所述硫酸灰渣和稀酸的重量比为1/15-1/6;在步骤S2)中,所述滤渣Ⅰ和稀酸的重量比为1/15-1/6,重复的次数为3次;所述稀酸的pH值为3-4。As a further improvement of the above technical solution, in step S1), the weight ratio of the sulfuric acid ash residue and dilute acid is 1/15-1/6; in step S2), the weight ratio of the filter residue I and the dilute acid is is 1/15-1/6, and the number of repetitions is 3; the pH of the dilute acid is 3-4.
作为上述技术方案的进一步改进,在步骤S3)中,所述滤渣Ⅱ与含有F-的稀酸的重量比为1:1,含有F-的稀酸中F-的浓度为0.15-0.3mg/L,含有F-的稀酸的pH值为3-4。As a further improvement of the above technical scheme, in step S3), the weight ratio of the filter residue II to the dilute acid containing F- is 1:1, and the concentration of F- in the dilute acid containing F- is 0.15-0.3 mg/ L, pH of dilute acid containing F- is 3-4 .
作为上述技术方案的进一步改进,在步骤S5)中,所述盐酸改性的活性碳与所述铊提取液Ⅰ的重量比为1/150000-1/40000。As a further improvement of the above technical solution, in step S5), the weight ratio of the hydrochloric acid-modified activated carbon to the thallium extract I is 1/150000-1/40000.
作为上述技术方案的进一步改进,在步骤S6)中,所述草酸铵溶液中草酸铵的浓度为40-60g/L,草酸铵溶液加热后的温度为50-60℃。As a further improvement of the above technical solution, in step S6), the concentration of ammonium oxalate in the ammonium oxalate solution is 40-60 g/L, and the temperature of the ammonium oxalate solution after heating is 50-60 °C.
作为上述技术方案的进一步改进,在步骤S7)中,所述氯化物为氯化钾,所述铊提取液Ⅱ中氯化钾的浓度为0.14-0.22mg/ml,所述铊提取液Ⅱ与所述Tl+洗脱液的体积比为1/16-1/10。As a further improvement of the above technical solution, in step S7), the chloride is potassium chloride, the concentration of potassium chloride in the thallium extraction solution II is 0.14-0.22 mg/ml, and the thallium extraction solution II and The volume ratio of the Tl + eluent is 1/16-1/10.
作为上述技术方案的进一步改进,在步骤S1)中,所述硫酸灰渣和所述稀酸的重量比为1/10,稀酸的pH值为3-4;As a further improvement of the above technical solution, in step S1), the weight ratio of the sulfuric acid ash and the dilute acid is 1/10, and the pH value of the dilute acid is 3-4;
在步骤S2)中,所述滤渣Ⅰ与所述稀酸的重量比为,重复的次数为3次;In step S2), the weight ratio of the filter residue I to the dilute acid is 3 times;
在步骤S3)中,所述滤渣Ⅱ与含有F-的稀酸的重量比为1/10,含有F-的稀酸中F-的浓度为0.20mg/L,含有F-的稀酸的pH值为3-4;In step S3), the weight ratio of the filter residue II to the dilute acid containing F- is 1/10 , the concentration of F- in the dilute acid containing F- is 0.20 mg/L, and the pH of the dilute acid containing F- The value is 3-4;
在步骤S5)中,所述盐酸改性的活性碳与所述铊提取液Ⅰ的重量比为1:80000;In step S5), the weight ratio of the hydrochloric acid-modified activated carbon to the thallium extract I is 1:80000;
在步骤S6)中,所述草酸铵溶液中草酸铵的浓度为50g/L,草酸铵溶液加热后的温度为50℃;In step S6), the concentration of ammonium oxalate in the ammonium oxalate solution is 50g/L, and the temperature after the ammonium oxalate solution is heated is 50°C;
在步骤S7)中,所述氯化物为氯化钾,所述Tl+洗脱液中氯化钾的浓度为0.17mg/ml,所述铊提取液Ⅱ与所述Tl+洗脱液的体积比1/15。In step S7), the chloride is potassium chloride, the concentration of potassium chloride in the Tl + eluent is 0.17 mg/ml, the volume of the thallium extract II and the Tl + eluent than 1/15.
本发明的有益效果在于:本发明提供一种界面作用的氯化亚铊的制备方法,本发明将意外发现TlF-TlF3非均相体系的类芬顿反应用于提取硫酸灰渣中Tl+,大大缩短了Tl+的提取时间;之后再以再用溴水氧化成Tl3+,盐酸改性的活性炭吸附Tl3+,草酸铵溶液洗脱并将Tl3+还原成Tl+,制备出更纯的TlCl;氯化亚铊的制备方法中采用的原料为硫酸生产过程的有害废料和常规试剂,制备方法简单、成本低价,而且具有“以废治废”的有益效果。The beneficial effects of the present invention are: the present invention provides a preparation method of interfacial thallium chloride, and the present invention will unexpectedly find that the Fenton-like reaction of the TlF - TlF heterogeneous system is used to extract Tl in the sulfuric ash residue , greatly shortened the extraction time of Tl + ; then oxidized to Tl 3+ with bromine water, adsorbed Tl 3+ with hydrochloric acid-modified activated carbon, eluted with ammonium oxalate solution and reduced Tl 3+ to Tl + , prepared The raw materials used in the preparation method of purer TlCl; thallium chloride are the harmful wastes and conventional reagents in the sulfuric acid production process, the preparation method is simple, the cost is low, and the beneficial effect of "using waste to treat waste" is obtained.
具体实施方式Detailed ways
为更好地说明本发明的目的、技术方案和优点,下面将结合具体实施例对本发明作进一步说明。In order to better illustrate the purpose, technical solutions and advantages of the present invention, the present invention will be further described below with reference to specific embodiments.
应当理解的是,本发明中采用术语“滤渣Ⅰ”、“滤渣Ⅱ”,“滤液Ⅰ”、“滤液Ⅱ”和“滤液Ш”,“铊提取液Ⅰ”、“铊提取液Ⅱ”等用来描述各种信息,但这些信息不应限于这些术语,这些术语仅用来将同一类型的信息彼此区分开。It should be understood that the terms "filter residue I", "filter residue II", "filtrate I", "filtrate II" and "filtrate Ш", "thallium extract I", "thallium extract II", etc. are used in the present invention. to describe various information, but the information should not be limited to these terms, which are only used to distinguish the same type of information from each other.
实施例1Example 1
本实施例提供一种基界面作用的氯化亚铊的制备方法,其依次包括以下步骤:The present embodiment provides a preparation method of thallium chloride acting on a base interface, which sequentially includes the following steps:
S1)将硫酸灰渣研磨粉碎,向硫酸灰渣中加入稀酸,搅拌振荡4-6h,过滤即得滤液Ⅰ和滤渣Ⅰ;S1) grinding and pulverizing the sulfuric acid ash residue, adding dilute acid to the sulfuric acid ash residue, stirring and shaking for 4-6h, and filtering to obtain filtrate I and filter residue I;
S2)向所述滤渣Ⅰ中继续加入稀酸,重复步骤S1)的操作,重复的次数至少为3次,即得滤液Ⅱ和滤渣Ⅱ;S2) continue to add dilute acid to described filter residue I, repeat the operation of step S1), and the number of repetitions is at least 3 times to obtain filtrate II and filter residue II;
S3)向所述滤渣Ⅱ中含有F-的稀酸,搅拌静置后过滤,即得滤液Ш;S3) in described filter residue II, contain the dilute acid of F- , after stirring and standing, filter, obtain filtrate Ш;
S4)合并所述滤液Ⅰ、所述滤液Ⅱ和所述滤液Ш,即得铊提取液Ⅰ;S4) merging the filtrate I, the filtrate II and the filtrate Ш to obtain the thallium extract I;
S5)向所述铊提取液Ⅰ中滴加溴水至微黄色,加入盐酸改性的活性碳,搅拌30-60min,过滤后即得活性炭混合物;S5) dropwise add bromine water to the thallium extract I until slightly yellow, add hydrochloric acid-modified activated carbon, stir for 30-60min, and filter to obtain an activated carbon mixture;
S6)用加热的草酸铵溶液分多次淋洗所述活性碳混合物,收集洗脱液即得Tl+洗脱液;S6) wash described activated carbon mixture with heated ammonium oxalate solution for several times, collect eluent and obtain T1 + eluent;
S7)向Tl+洗脱液中加入氯化物,搅拌、加热浓缩,即得铊提取液Ⅱ;对铊提取液Ⅱ进行冷却、干燥,即得TlCl晶体;S7) adding chloride to the Tl + eluent, stirring, heating and concentrating to obtain thallium extract II; cooling and drying the thallium extract II to obtain TlCl crystals;
在步骤S1)中,硫酸灰渣和稀酸的重量比为1/15-1/6;在步骤S2)中,滤渣Ⅰ和稀酸的重量比为1/15-1/6,重复的次数为3次;稀酸的pH值为3-4;在步骤S3)中,滤渣Ⅱ与含有F-的稀酸的重量比1:1,含有F-的稀酸中F-的浓度为0.15~0.30mg/L,含有F-的稀酸的pH值为3-4;在步骤S5)中,盐酸改性的活性碳与铊提取液Ⅰ的质量比为1/40000-1/150000;在步骤S6)中,草酸铵溶液中草酸铵的浓度为40-60g/L,草酸铵溶液加热后的温度为50-60℃;在步骤S7)中,铊提取液Ⅱ与Tl+洗脱液的体积比为1/16-1/10。In step S1), the weight ratio of sulfuric acid ash residue and dilute acid is 1/15-1/6; in step S2), the weight ratio of filter residue I and dilute acid is 1/15-1/6, and the number of repetitions The pH value of the dilute acid is 3-4; in step S3), the weight ratio of the filter residue II to the dilute acid containing F- is 1:1, and the concentration of F- in the dilute acid containing F- is 0.15~ 0.30mg/L, the pH value of the dilute acid containing F- is 3-4; in step S5), the mass ratio of hydrochloric acid-modified activated carbon to thallium extract I is 1/40000-1/150000; in step S5) In S6), the concentration of ammonium oxalate in the ammonium oxalate solution is 40-60 g/L, and the temperature after the ammonium oxalate solution is heated is 50-60 °C; in step S7), the volume of thallium extract II and Tl + eluent The ratio is 1/16-1/10.
优选地,氯化物为氯化钾,铊提取液Ⅱ中氯化钾的浓度为0.14-0.22mg/ml。Preferably, the chloride is potassium chloride, and the concentration of potassium chloride in the thallium extract II is 0.14-0.22 mg/ml.
实施例2Example 2
本实施例提供一种基界面作用的氯化亚铊的制备方法,其依次包括以下步骤:The present embodiment provides a preparation method of thallium chloride acting on a base interface, which sequentially includes the following steps:
S1)将硫酸灰渣研磨粉碎,过200目筛网(粉碎后硫酸灰渣的粒径≤0.08mm);取粉碎的硫酸灰渣10kg,按固:液重量比=1:6加入pH值为3的盐酸,搅拌振荡6h,过滤即得滤液Ⅰ和滤渣Ⅰ;S1) grind and pulverize the sulfuric acid ash, pass through a 200-mesh sieve (the particle size of the sulfuric acid ash after pulverization is less than or equal to 0.08mm); take 10kg of the pulverized sulfuric acid ash, add the pH value according to the solid:liquid weight ratio=1:6 3% of hydrochloric acid, stirred and shaken for 6h, and filtered to obtain filtrate I and filter residue I;
S2)按固:液重量比比=1:6向滤渣Ⅰ中继续加入pH值为3的盐酸,重复步骤S1)的操作3次,即得滤液Ⅱ和滤渣Ⅱ;S2) continue to add the hydrochloric acid with pH value of 3 in filter residue I according to solid: liquid weight ratio=1:6, repeat the operation of step S1) 3 times, namely obtain filtrate II and filter residue II;
S3)按固:液重量比=1:1向滤渣Ⅱ中加入含有0.3mg/L F-且pH值为3的盐酸,搅拌静置后过滤,即得滤液Ш;S3) add the hydrochloric acid containing 0.3mg/LF- and pH value of 3 to filter residue II according to solid: liquid weight ratio=1:1, stir after standing and filter to obtain filtrate Ш;
S4)合并滤液Ⅰ、滤液Ⅱ和滤液Ш,即得铊提取液Ⅰ;S4) merge filtrate I, filtrate II and filtrate Ш to obtain thallium extract I;
S5)向铊提取液Ⅰ中滴加溴水至微黄色,加入盐酸改性的活性碳,搅拌50min,过滤后即得活性炭混合物;盐酸改性的活性碳与铊提取液Ⅰ的重量比为1:90000;S5) dropwise add bromine water to the thallium extract I until light yellow, add hydrochloric acid-modified activated carbon, stir for 50min, and filter to obtain an activated carbon mixture; the weight ratio of the hydrochloric acid-modified activated carbon to the thallium extract I is 1 : 90000;
S6)用53℃的草酸铵溶液分多次淋洗活性碳混合物,收集洗脱液即得Tl+洗脱液;草酸铵溶液中草酸铵的浓度为52g/L;S6) wash the activated carbon mixture with the ammonium oxalate solution of 53 DEG C for several times, collect the eluate to obtain T1 + eluate; the concentration of ammonium oxalate in the ammonium oxalate solution is 52g/L;
S7)向Tl+洗脱液中加入氯化钾,Tl+洗脱液中氯化钾浓度为0.2mg/mL;搅拌、加热浓缩,即得铊提取液Ⅱ,铊提取液Ⅱ与Tl+洗脱液的体积比为1/10;对铊提取液Ⅱ进行冷却、干燥,即得TlCl晶体。S7) add potassium chloride to Tl + eluent, the potassium chloride concentration in Tl + eluent is 0.2 mg/mL; stir, heat and concentrate, namely obtain thallium extract II, thallium extract II and Tl + wash The volume ratio of deliquoring is 1/10; the thallium extract II is cooled and dried to obtain TlCl crystals.
实施例3Example 3
本实施例提供一种基界面作用的氯化亚铊的制备方法,其依次包括以下步骤:The present embodiment provides a preparation method of thallium chloride acting on a base interface, which sequentially includes the following steps:
S1)将硫酸灰渣研磨粉碎,过200目筛网(粉碎后硫酸灰渣的粒径≤0.08mm);取粉碎的硫酸灰渣10kg,按固:液重量比=1:12.5加入pH值为3的硫酸,搅拌振荡6h,过滤即得滤液Ⅰ和滤渣Ⅰ;S1) grind and pulverize the sulfuric acid ash, pass through a 200-mesh sieve (the particle size of the sulfuric acid ash after pulverization is less than or equal to 0.08mm); take 10kg of the pulverized sulfuric acid ash, add the pH value according to the solid:liquid weight ratio=1:12.5 3% of sulfuric acid, stirred and shaken for 6h, and filtered to obtain filtrate I and filter residue I;
S2)按固:液比重量=1:12.5向滤渣Ⅰ中继续加入pH值为3的硫酸,重复步骤S1)的操作3次,即得滤液Ⅱ和滤渣Ⅱ;S2) continue to add the sulfuric acid with pH value of 3 in filter residue I according to solid:liquid ratio weight=1:12.5, repeat the operation of step S1) 3 times to obtain filtrate II and filter residue II;
S3)按固:液重量比=1:1向滤渣Ⅱ中加入含有0.15mg/L F-且pH值为3的硫酸,搅拌静置后过滤,即得滤液Ш;S3) add sulfuric acid containing 0.15mg/LF- and pH value 3 to filter residue II according to solid: liquid weight ratio=1:1, stir after standing, and filter to obtain filtrate Ш;
S4)合并滤液Ⅰ、滤液Ⅱ和滤液Ш,即得铊提取液Ⅰ;S4) merge filtrate I, filtrate II and filtrate Ш to obtain thallium extract I;
S5)向铊提取液Ⅰ中滴加溴水至微黄色,加入盐酸改性的活性碳,搅拌50min,过滤后即得活性炭混合物;盐酸改性的活性碳与铊提取液Ⅰ的重量比为1:100000;S5) dropwise add bromine water to the thallium extract I until light yellow, add hydrochloric acid-modified activated carbon, stir for 50min, and filter to obtain an activated carbon mixture; the weight ratio of the hydrochloric acid-modified activated carbon to the thallium extract I is 1 : 100000;
S6)用50℃的草酸铵溶液分多次淋洗所述活性碳混合物,收集洗脱液即得Tl+洗脱液;草酸铵溶液中草酸铵的浓度为45g/L;S6) wash described activated carbon mixture with the ammonium oxalate solution of 50 ℃ for several times, collect eluent and obtain T1 + eluent; the concentration of ammonium oxalate in ammonium oxalate solution is 45g/L;
S7)向Tl+洗脱液中加入氯化钾,Tl+洗脱液中氯化钾浓度为0.22mg/mL;搅拌、加热浓缩,即得铊提取液Ⅱ,铊提取液Ⅱ与Tl+洗脱液的体积比为1/12;对铊提取液Ш进行冷却、干燥,即得TlCl晶体。S7) add potassium chloride to Tl + eluent, the potassium chloride concentration in Tl + eluent is 0.22mg/mL; stir, heat and concentrate, namely obtain thallium extract II, thallium extract II and Tl + wash The volume ratio of deliquoring is 1/12; the thallium extraction solution Ш is cooled and dried to obtain TlCl crystals.
对比例1Comparative Example 1
本对比例提供一种氯化亚铊的制备方法,其与实施例3制备方法的区别点在于:在步骤S1)中,取粉碎的硫酸灰渣10kg,按固:液重量比=1:5加入pH 1-2的硫酸废水,搅拌24h后过滤,即得铊提取液Ⅰ;剩余步骤采用实施例2制备方法步骤S5)~S7)。This comparative example provides a preparation method of thallium chloride, which is different from the preparation method of Example 3 in that: in step S1), 10kg of crushed sulfuric acid ash is taken, and the weight ratio of solid:liquid=1:5 Sulfuric acid wastewater with pH 1-2 is added, stirred for 24 hours and filtered to obtain thallium extract I; the remaining steps are steps S5) to S7) of the preparation method in Example 2.
实施例3和对比例1采用的原料中,硫酸灰渣和硫酸废水来自云浮硫酸厂,硫酸废水中铊的含量为0.28mg/kg,硫酸灰渣中铊的含量为49mg/kg,硫酸灰渣包含以下重量百分含量的组分:Fe2O3 38%、Fe3O448%和SiO213%。对实施例3和对比例1制备的氯化亚铊晶体进行产率和纯度测定,实施例3制备出TlCl晶体为53mg、TlCl纯度为94%,对比例1制备出TlCl晶体为27mg、TlCl纯度为93%,短时间内提取的TlCl晶体较少。In the raw material that embodiment 3 and comparative example 1 adopt, sulfuric acid ash residue and sulfuric acid waste water come from Yunfu Sulfuric Acid Factory, and the content of thallium in the sulfuric acid waste water is 0.28mg/kg, and the content of thallium in the sulfuric acid ash residue is 49mg/kg, and the sulfuric acid ash residue is 49 mg/kg. Contains the following components by weight: Fe 2 O 3 38%, Fe 3 O 4 48% and SiO 2 13%. The yield and purity of the thallium chloride crystals prepared in Example 3 and Comparative Example 1 were measured. The TlCl crystal prepared in Example 3 was 53 mg and the TlCl purity was 94%. The TlCl crystal prepared in Comparative Example 1 was 27 mg and the TlCl purity was 94%. was 93%, and less TlCl crystals were extracted in a short time.
对比例1采用的是中国发明专利“一种碘化亚铊的制备方法”(申请号为201810264009.1,申请日为2018年3月28日)中Tl+的提取方法,尽管对比例1制备方法所用的硫酸废水可引入少量的铊,但是实施例3制备方法中稀酸的pH值为3时,硫酸灰渣的亚铁物种以Fe(OH)+和Fe(OH)2 0水解并吸附电负性强的F-,其反应活性较pH值1-2时亚铁物种以Fe2+溶解时显著增强;另外,在对比例1中制备方法中,硫酸废水酸解时,将从硫酸灰渣和硫酸废水中引入较多的共存离子,对比例1制备纯度较低的氯化亚铊。What comparative example 1 adopts is the extraction method of Tl in Chinese invention patent "a kind of preparation method of thallium iodide" (application number is 201810264009.1, the application date is March 28, 2018 ) , although comparative example 1 preparation method is used The sulfuric acid wastewater can introduce a small amount of thallium, but when the pH value of the dilute acid in the preparation method of Example 3 is 3, the ferrous species of the sulfuric acid ash is hydrolyzed with Fe(OH) + and Fe(OH) 2 0 and adsorbs electronegativity F - , which has strong reactivity, has a significantly enhanced reactivity than when the ferrous species is dissolved in Fe 2+ at pH 1-2; in addition, in the preparation method in Comparative Example 1, when the sulfuric acid wastewater is acidly hydrolyzed, the sulfuric acid ash will be removed from the slag. With the introduction of more coexisting ions into sulfuric acid wastewater, comparative example 1 prepares thallium chloride with lower purity.
实施例4Example 4
本实施例提供一种基界面作用的氯化亚铊的制备方法,其依次包括以下步骤:The present embodiment provides a preparation method of thallium chloride acting on a base interface, which sequentially includes the following steps:
S1)将硫酸灰渣研磨粉碎,过200目筛网(粉碎后硫酸灰渣的粒径≤0.08mm);取粉碎的硫酸灰渣10kg,按固:液重量比=1:10加入pH值为3.5的硝酸,搅拌振荡4h,过滤即得滤液Ⅰ和滤渣Ⅰ;S1) grind and pulverize the sulfuric acid ash, pass through a 200-mesh sieve (the particle size of the sulfuric acid ash after pulverization is less than or equal to 0.08mm); get 10kg of the pulverized sulfuric acid ash, add the pH value according to the solid:liquid weight ratio=1:10. 3.5% of nitric acid, stirred and shaken for 4h, and filtered to obtain filtrate I and filter residue I;
S2)按固:液重量比=1:10向滤渣Ⅰ中继续加入pH值为3.5的硝酸,重复步骤S1)的操作3次,即得滤液Ⅱ和滤渣Ⅱ;S2) continue to add the nitric acid with pH value of 3.5 in filter residue I according to the solid: liquid weight ratio=1:10, repeat the operation of step S1) 3 times, namely obtain filtrate II and filter residue II;
S3)按固:液重量比=1:1向滤渣Ⅱ中加入含有0.20mg/L F-且pH值为3.5的硝酸,搅拌静置后过滤,即得滤液Ш;S3) add the nitric acid that contains 0.20mg / LF- and pH value is 3.5 to filter residue II according to solid: liquid weight ratio=1:1, stir and filter after standing to obtain filtrate Ш;
S4)合并滤液Ⅰ、滤液Ⅱ和滤液Ш,即得铊提取液Ⅰ;S4) merge filtrate I, filtrate II and filtrate Ш to obtain thallium extract I;
S5)向铊提取液Ⅰ中滴加溴水至微黄色,加入盐酸改性的活性碳,搅拌40min,过滤后即得活性炭混合物;盐酸改性的活性碳与铊提取液Ⅰ的重量比为1:80000;S5) dropwise add bromine water to the thallium extract I until light yellow, add hydrochloric acid-modified activated carbon, stir for 40 min, and filter to obtain an activated carbon mixture; the weight ratio of the hydrochloric acid-modified activated carbon to the thallium extract I is 1 : 80000;
S6)用50℃的草酸铵溶液分多次淋洗活性碳混合物,收集洗脱液即得Tl+洗脱液;草酸铵溶液中草酸铵的浓度为50g/L;S6) wash the activated carbon mixture with the ammonium oxalate solution of 50 DEG C for several times, collect the eluate to obtain T1 + eluate; the concentration of ammonium oxalate in the ammonium oxalate solution is 50g/L;
S7)向Tl+洗脱液中加入氯化钾,Tl+洗脱液中氯化钾浓度为0.17mg/mL;搅拌、加热浓缩,即得铊提取液Ⅱ,铊提取液Ⅱ与Tl+洗脱液的体积比为1/15;对铊提取液Ⅱ进行冷却、干燥,即得TlCl晶体。S7) add potassium chloride to Tl + eluent, the potassium chloride concentration in Tl + eluent is 0.17mg/mL; stir, heat and concentrate, namely obtain thallium extract II, thallium extract II and Tl + wash The volume ratio of deliquoring is 1/15; the thallium extract II is cooled and dried to obtain TlCl crystals.
对比例2Comparative Example 2
本对比例提供一种氯化亚铊的制备方法,其与实施例制备方法5的区别点在于:在步骤S1)中,取粉碎的硫酸灰渣10kg,按固:液重量比=1:3加入pH 1-2的硫酸废水,搅拌16h后过滤,即得铊提取液Ⅰ;剩余步骤采用实施例4制备方法步骤S5)~S7)。This comparative example provides a preparation method of thallium chloride, which is different from the preparation method 5 of the embodiment in that: in step S1), 10kg of crushed sulfuric acid ash is taken, and the weight ratio of solid:liquid = 1:3 Sulfuric acid wastewater with pH 1-2 was added, stirred for 16 hours and filtered to obtain thallium extract I; the remaining steps were steps S5) to S7) of the preparation method in Example 4.
实施例4和对比例2采用的原料中,硫酸灰渣和硫酸废水来自云浮硫酸厂,硫酸废水中铊的含量为0.29mg/kg,硫酸灰渣中铊的含量为40mg/kg,硫酸灰渣包含以下重量百分含量的组分:Fe2O3 49%、Fe3O4 41%和SiO2 9.5%。对实施例5和对比例2制备的氯化亚铊晶体进行产率和纯度测定,实施例4制备出TlCl晶体为49mg、TlCl纯度为94%,对比例2制备出TlCl晶体为9mg、TlCl纯度为93%。In the raw material that embodiment 4 and comparative example 2 adopt, sulfuric acid ash residue and sulfuric acid waste water come from Yunfu Sulfuric Acid Factory, the content of thallium in the sulfuric acid waste water is 0.29mg/kg, and the content of thallium in the sulfuric acid ash residue is 40mg/kg, and the sulfuric acid ash residue is 40 mg/kg. Contains the following components by weight: Fe 2 O 3 49%, Fe 3 O 4 41% and SiO 2 9.5%. The yield and purity of the thallium chloride crystals prepared in Example 5 and Comparative Example 2 were measured. The TlCl crystals prepared in Example 4 were 49 mg and the TlCl purity was 94%. The TlCl crystals prepared in Comparative Example 2 were 9 mg and the TlCl purity was 94%. was 93%.
实施例5Example 5
本实施例提供一种基界面作用的氯化亚铊的制备方法,其依次包括以下步骤:The present embodiment provides a preparation method of thallium chloride acting on a base interface, which sequentially includes the following steps:
S1)将硫酸灰渣研磨粉碎,过200目筛网(粉碎后硫酸灰渣的粒径≤0.08mm);取粉碎的硫酸灰渣10kg,按固:液比=1:15加入pH值为4的硫酸,搅拌振荡5h,过滤即得滤液Ⅰ和滤渣Ⅰ;S1) grind and pulverize the sulfuric acid ash, pass through a 200-mesh sieve (the particle size of the sulfuric acid ash after pulverization is less than or equal to 0.08mm); take 10kg of the pulverized sulfuric acid ash, add the pH value to 4 according to the solid:liquid ratio=1:15 of sulfuric acid, stirred and shaken for 5h, and filtered to obtain filtrate I and filter residue I;
S2)按固:液重量比=1:15向滤渣Ⅰ中继续加入pH值为4的硫酸,重复步骤S1)的操作3次,即得滤液Ⅱ和滤渣Ⅱ;S2) continue to add sulfuric acid with pH value of 4 to filter residue I according to solid: liquid weight ratio=1:15, repeat the operation of step S1) 3 times, namely obtain filtrate II and filter residue II;
S3)按固:液重量比=1:1向滤渣Ⅱ中加入含有0.25mg/L F-且pH值为4的硫酸,搅拌静置后过滤,即得滤液Ш;S3) add the sulfuric acid that contains 0.25mg/LF- and pH value is 4 to filter residue II according to solid: liquid weight ratio=1:1, stir after standing and filter to obtain filtrate Ш;
S4)合并滤液Ⅰ、滤液Ⅱ和滤液Ш,即得铊提取液Ⅰ;S4) merge filtrate I, filtrate II and filtrate Ш to obtain thallium extract I;
S5)向铊提取液Ⅰ中滴加溴水至微黄色,加入盐酸改性的活性碳,搅拌40min,过滤后即得活性炭混合物;盐酸改性的活性碳与铊提取液Ⅰ的重量比为1:150000;S5) dropwise add bromine water to the thallium extract I until light yellow, add hydrochloric acid-modified activated carbon, stir for 40 min, and filter to obtain an activated carbon mixture; the weight ratio of the hydrochloric acid-modified activated carbon to the thallium extract I is 1 : 150000;
S6)用60℃的草酸铵溶液分多次淋洗活性碳混合物,收集洗脱液即得Tl+洗脱液;草酸铵溶液中草酸铵的浓度为40g/L;S6) wash the activated carbon mixture with the ammonium oxalate solution of 60 DEG C for several times, collect the eluate to obtain T1 + eluate; the concentration of ammonium oxalate in the ammonium oxalate solution is 40g/L;
S7)向Tl+洗脱液中加入氯化钾,Tl+洗脱液中氯化钾浓度为0.14mg/mL;搅拌、加热浓缩,即得铊提取液Ⅱ,铊提取液Ⅱ与Tl+洗脱液的体积比为1/16;对铊提取液Ⅱ进行冷却、干燥,即得TlCl晶体。S7) add potassium chloride to Tl + eluent, the potassium chloride concentration in Tl + eluent is 0.14mg/mL; stir, heat and concentrate, namely obtain thallium extract II, thallium extract II and Tl + wash The volume ratio of deliquoring is 1/16; the thallium extract II is cooled and dried to obtain TlCl crystals.
对比例3Comparative Example 3
本对比例提供一种氯化亚铊的制备方法,其与实施例制备方法5的区别点在于:在步骤S1)中,取粉碎的硫酸灰渣10kg,按固:液重量比=1:6加入pH 1-2的硫酸废水,搅拌20h后过滤,即得得铊提取液Ⅰ;剩余步骤采用实施例5制备方法步骤S5)~S7)。This comparative example provides a preparation method of thallium chloride, which is different from the preparation method 5 of the embodiment in that: in step S1), 10 kg of crushed sulfuric acid ash is taken, and the solid:liquid weight ratio=1:6 Sulfuric acid wastewater with pH 1-2 was added, stirred for 20 hours and filtered to obtain thallium extract I; the remaining steps were steps S5) to S7) of the preparation method in Example 5.
实施例5和对比例3采用的原料中,硫酸灰渣和硫酸废水来自云浮硫酸厂,硫酸废水中铊的含量为0.32mg/kg,硫酸灰渣中铊的含量为51mg/kg,硫酸灰渣包含以下重量百分含量的组分:Fe2O3 30%、Fe3O4 40%和SiO2 20%。对实施例5和对比例3制备的氯化亚铊晶体进行产率和纯度测定,实施例5制备出TlCl晶体为39mg、TlCl纯度为93%,对比例3制备出TlCl晶体为27mg、TlCl纯度为92.5%。In the raw material that embodiment 5 and comparative example 3 adopt, sulfuric acid ash residue and sulfuric acid waste water come from Yunfu Sulfuric Acid Factory, and the content of thallium in the sulfuric acid waste water is 0.32 mg/kg, and the content of thallium in the sulfuric acid ash residue is 51 mg/kg, and the sulfuric acid ash residue is 51 mg/kg. Contains the following components by weight: Fe 2 O 3 30%, Fe 3 O 4 40% and SiO 2 20%. The yield and purity of the thallium chloride crystals prepared in Example 5 and Comparative Example 3 were measured. The TlCl crystal prepared in Example 5 was 39 mg and the TlCl purity was 93%. The TlCl crystal prepared in Comparative Example 3 was 27 mg and the TlCl purity was 93%. was 92.5%.
实施例6Example 6
本实施例提供一种基界面作用的氯化亚铊的制备方法,其依次包括以下步骤:The present embodiment provides a preparation method of thallium chloride acting on a base interface, which sequentially includes the following steps:
S1)将硫酸灰渣研磨粉碎,过200目筛网(粉碎后硫酸灰渣的粒径≤0.08mm);取粉碎的硫酸灰渣10kg,按固:液重量比=1:10加入pH值为3.5的硝酸,搅拌振荡4.5h,过滤即得滤液Ⅰ和滤渣Ⅰ;S1) grind and pulverize the sulfuric acid ash, pass through a 200-mesh sieve (the particle size of the sulfuric acid ash after pulverization is less than or equal to 0.08mm); get 10kg of the pulverized sulfuric acid ash, add the pH value according to the solid:liquid weight ratio=1:10. 3.5% of nitric acid, stir and shake for 4.5h, and filter to obtain filtrate I and filter residue I;
S2)按固:液重量比=1:10向滤渣Ⅰ中继续加入pH值为3.5的硝酸,重复步骤S1)的操作3次,即得滤液Ⅱ和滤渣Ⅱ;S2) continue to add the nitric acid with pH value of 3.5 in filter residue I according to the solid: liquid weight ratio=1:10, repeat the operation of step S1) 3 times, namely obtain filtrate II and filter residue II;
S3)按固:液重量比=1:1向滤渣Ⅱ中加入含有0.25mg/L F-且pH值为3.5的硝酸,搅拌静置后过滤,即得滤液Ш;S3) add the nitric acid containing 0.25mg/LF- and pH value of 3.5 to filter residue II according to solid: liquid weight ratio=1:1, stir and stand and filter to obtain filtrate Ш;
S4)合并滤液Ⅰ、滤液Ⅱ和滤液Ш,即得铊提取液Ⅰ;S4) merge filtrate I, filtrate II and filtrate Ш to obtain thallium extract I;
S5)向铊提取液Ⅰ中滴加溴水至微黄色,加入盐酸改性的活性碳,搅拌30min,过滤后即得活性炭混合物;盐酸改性的活性碳与铊提取液Ⅰ的重量比为1:40000;S5) dropwise add bromine water to the thallium extract I until slightly yellow, add hydrochloric acid-modified activated carbon, stir for 30min, and filter to obtain an activated carbon mixture; the weight ratio of the hydrochloric acid-modified activated carbon to the thallium extract I is 1 : 40000;
S6)用50℃的草酸铵溶液分多次淋洗所述活性碳混合物,收集洗脱液即得Tl+洗脱液;草酸铵溶液中草酸铵的浓度为60g/L;S6) wash described activated carbon mixture with the ammonium oxalate solution of 50 ℃ for several times, collect eluent and obtain T1 + eluent; the concentration of ammonium oxalate in ammonium oxalate solution is 60g/L;
S7)向Tl+洗脱液中加入氯化钾,Tl+洗脱液中加入氯化钾浓度为0.16mg/mL;搅拌、加热浓缩,即得铊提取液Ⅱ,铊提取液Ⅱ与Tl+洗脱液的体积比1/16;对铊提取液Ⅱ进行冷却、干燥,即得TlCl晶体。S7) adding potassium chloride to the Tl + eluent, the concentration of adding potassium chloride to the Tl + eluent is 0.16 mg/mL; stirring, heating and concentrating to obtain thallium extract II, thallium extract II and Tl + The volume ratio of the eluent is 1/16; the thallium extract II is cooled and dried to obtain TlCl crystals.
对比例4Comparative Example 4
本对比例提供一种氯化亚铊的制备方法,其与实施例制备方法6的区别点在于:在步骤S1)中,取粉碎的硫酸灰渣10kg,按固:液重量比=1:2加入pH 1-2的硫酸废水,搅拌18h后过滤,即得得铊提取液Ⅰ;剩余步骤采用实施例6制备方法步骤S5)~S7)。This comparative example provides a preparation method of thallium chloride, which is different from the preparation method 6 of the embodiment in that: in step S1), 10kg of crushed sulfuric acid ash is taken, and the weight ratio of solid:liquid = 1:2 Sulfuric acid waste water with pH 1-2 is added, stirred for 18 hours and filtered to obtain thallium extract I; the remaining steps adopt steps S5) to S7) of the preparation method in Example 6.
实施例6和对比例4采用的原料中,硫酸灰渣和硫酸废水来自云浮硫酸厂,硫酸废水中铊的含量为0.34mg/kg,硫酸灰渣中铊的含量为57mg/kg,硫酸灰渣包含以下重量百分含量的组分:Fe2O3 33%、Fe3O4 35%和SiO2 20%。对实施例6和对比例4制备的氯化亚铊晶体进行产率和纯度测定,实施例6制备出TlCl晶体为49mg、TlCl纯度为95%,对比例1制备出TlCl晶体为12.5mg、TlCl纯度为93%。In the raw material that embodiment 6 and comparative example 4 adopt, sulfuric acid ash residue and sulfuric acid waste water come from Yunfu Sulfuric Acid Factory, and the content of thallium in the sulfuric acid waste water is 0.34mg/kg, and the content of thallium in the sulfuric acid ash residue is 57mg/kg, and the sulfuric acid ash residue is 57 mg/kg. Contains the following components by weight: Fe 2 O 3 33%, Fe 3 O 4 35% and SiO 2 20%. The yield and purity of the thallium chloride crystals prepared in Example 6 and Comparative Example 4 were measured. The TlCl crystals prepared in Example 6 were 49 mg, and the TlCl purity was 95%. The TlCl crystals prepared in Comparative Example 1 were 12.5 mg and TlCl. The purity is 93%.
综上可知,本发明实施例和对比例在硫酸灰渣用量和提取时间相同时,由于Tl+提取方法的差异,本发明所得氯化亚铊的量和纯度均优于对比例。To sum up, when the sulfuric acid ash residue consumption and extraction time are the same in the embodiment of the present invention and the comparative example, due to the difference of the Tl + extraction method, the amount and purity of the thallium chloride obtained in the present invention are better than those of the comparative example.
本发明仅列出实施例3~6制备出TlCl晶体进行产率和纯度,本发明其他实施例也可以取得类似于实施例3~6的实验效果。The present invention only lists the yield and purity of TlCl crystals prepared in Examples 3 to 6, and other embodiments of the present invention can also achieve experimental results similar to those of Examples 3 to 6.
最后所应当说明的是,以上实施例用以说明本发明的技术方案而非对本发明保护范围的限制,尽管参照较佳实施例对本发明作了详细说明,本领域的普通技术人员应当理解,可以对本发明的技术方案进行修改或者同等替换,而不脱离本发明技术方案的实质和范围。Finally, it should be noted that the above embodiments are used to illustrate the technical solutions of the present invention rather than to limit the protection scope of the present invention. Although the present invention has been described in detail with reference to the preferred embodiments, those of ordinary skill in the art should The technical solutions of the present invention can be modified or equivalently replaced without departing from the spirit and scope of the technical solutions of the present invention.
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