CN115304105B - A method for hydrothermal solidification of arsenic-rich crystals - Google Patents
A method for hydrothermal solidification of arsenic-rich crystals Download PDFInfo
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Abstract
Description
技术领域Technical field
本发明涉及有色金属冶炼中含砷副产物无毒无害化领域,特别是采用水热固化锑冶炼砷碱渣资源化利用中砷酸钠结晶物的方法。The present invention relates to the field of non-toxic and harmless treatment of arsenic-containing by-products in non-ferrous metal smelting, particularly a method for utilizing hydrothermal solidification of antimony to smelt sodium arsenate crystals for resource utilization of arsenic-alkali slag.
背景技术Background technique
砷在锑冶炼砷碱渣中主要以砷酸钠和亚砷酸钠存在,其含量在5~20%。在砷碱渣资源化利用中,砷富集于浸出液,经过浓缩结晶或分步结晶产出砷酸钠结晶物。由于只有少量砷可用于化工及半导体领域,产品市场小,大量砷酸钠结晶物只能长期堆放。剧毒性砷酸钠易溶于水,在长期堆放中存在被雨水渗透,造成严重的砷污染,对有色金属冶炼含砷副产物清洁化利用造成极大的环保压力。Arsenic mainly exists in the form of sodium arsenate and sodium arsenite in the arsenic-alkali residue of antimony smelting, with its content ranging from 5 to 20%. In the resource utilization of arsenic-alkali residue, arsenic is enriched in the leachate, and sodium arsenate crystals are produced through concentrated crystallization or fractional crystallization. Since only a small amount of arsenic can be used in the chemical and semiconductor fields and the product market is small, large amounts of sodium arsenate crystals can only be piled up for a long time. Highly toxic sodium arsenate is easily soluble in water and may be penetrated by rainwater during long-term storage, causing serious arsenic pollution and placing great environmental pressure on the clean utilization of arsenic-containing by-products of non-ferrous metal smelting.
臭葱石(FeAsO4·2H2O)是一种高度结晶性砷酸铁,主要呈现双锥状、柱状、晶簇状或葡萄状等,单晶粒径为0.1~0.5mm,呈现粒径为3~5mm的粒状集合体,密度为3.10g/cm3,其颜色主要有浅绿色、淡黄色、白色等。正八面体臭葱石晶体参数为Z=8的斜方晶系,空间群为Pcab。臭葱石的标准生成焓为-1508.9kJ/mol,标准熵为188.0J·mol-1·K-1,吉布斯自由能为-1284.8kJ/mol,溶度积仅为(log Ksp=-26.4)无定型砷酸铁(log Ksp=-23.0)的千分之一。自然环境下的臭葱石为毒砂矿物的风化产物,能在大自然中稳定存在,主要表现为在酸性介质中以FeAsO4·2H2O存在,在碱性环境形成FeAsO4·2H2O@FeOOH核壳型稳定结构。臭葱石具有晶体结构稳定,含砷量高(32.5%),渣量小,易过滤,无毒和存放费用低等优点。Scorodite (FeAsO 4 ·2H 2 O) is a highly crystalline iron arsenate, mainly in the form of bipyramids, columns, clusters or grapes, etc., with a single crystal particle size of 0.1 to 0.5 mm. It is a granular aggregate of 3 to 5 mm with a density of 3.10g/cm 3 and its colors are mainly light green, light yellow, white, etc. The crystal parameters of octahedral scorodite are It is an orthorhombic crystal system with Z=8 and its space group is Pcab. The standard enthalpy of formation of scorodite is -1508.9kJ/mol, the standard entropy is 188.0J·mol -1 ·K -1 , the Gibbs free energy is -1284.8kJ/mol, and the solubility product is only (log K sp = -26.4) One thousandth of amorphous iron arsenate (log K sp = -23.0). Scorodite in the natural environment is the weathering product of arsenopyrite minerals and can exist stably in nature. It mainly exists as FeAsO 4 ·2H 2 O in acidic media and forms FeAsO 4 ·2H 2 O in alkaline environments. @FeOOH core-shell stable structure. Scorodite has the advantages of stable crystal structure, high arsenic content (32.5%), small slag content, easy filtering, non-toxicity and low storage cost.
目前公布的专利中,专利CN 109809494 A公布了一种稳定化处理砷碱渣制备臭葱石的固砷方法,通过氧化浸出回收锑,然后通入CO2脱碱,产出含有砷酸钠的溶液加酸调节pH=1.0~2.5,加入亚铁盐和H2O2混合溶液后加热反应合成出双锥八面体臭葱石晶体,如化学反应式(1)。该方法能有效固化砷碱渣中砷为无毒的臭葱石晶体,但反应终点pH下降明显,形成酸的累积效应,导致固砷效果变差。该方法仅适合砷浓度低于20g/L的溶液合成臭葱石,增加固砷后液处理负担。Among the currently published patents, patent CN 109809494 A discloses an arsenic fixation method for preparing scorodite by stabilizing arsenic-alkali residue. The antimony is recovered through oxidative leaching, and then CO 2 is introduced for dealkalization to produce sodium arsenate. Add acid to the solution to adjust the pH = 1.0 to 2.5. Add a mixed solution of ferrous salt and H 2 O 2 and then heat to react to synthesize bipyramidal octahedral scorodite crystals, as shown in chemical reaction formula (1). This method can effectively solidify arsenic in arsenic-alkali residue into non-toxic scorodite crystals, but the pH at the end of the reaction drops significantly, forming a cumulative effect of acid, resulting in poor arsenic fixation effect. This method is only suitable for synthesizing scorodite from solutions with arsenic concentration lower than 20g/L, which increases the burden of post-arsenic solidification liquid treatment.
2Fe2++2H3AsO4+H2O2+2H2O=2FeAsO4·2H2O+4H+ (1)2Fe 2+ +2H 3 AsO 4 +H 2 O 2 +2H 2 O=2FeAsO 4 ·2H 2 O+4H + (1)
发明内容Contents of the invention
为了解决砷碱渣中砷酸钠结晶物合成臭葱石中酸累积、固砷效果差和固砷后液排放对环境造成的危害。本发明的第一个目的在于提供一种固体三价铁盐在水热反应中高效合成臭葱石晶体,实现砷酸钠结晶物固化和适合于长期安全储存。该方法具有固砷效果良好、适合于高砷溶液、合成前后溶液pH变化小,无H+积累。In order to solve the environmental hazards caused by acid accumulation in the synthesis of scorodite from sodium arsenate crystals in arsenic-alkali residues, poor arsenic fixation effect and discharge of arsenic fixation liquid. The first object of the present invention is to provide a solid ferric salt that can efficiently synthesize scorodite crystals in a hydrothermal reaction, achieve solidification of sodium arsenate crystals, and be suitable for long-term safe storage. This method has good arsenic fixation effect, is suitable for high arsenic solutions, has small pH changes of the solution before and after synthesis, and has no H + accumulation.
本发明的第二个目的在于采用中和沉淀法深度去除固砷后液中砷铁离子,获得的砷铁盐用于水热合成臭葱石。中和沉淀法具有砷铁去除彻底、砷铁盐可回用的优点。The second object of the present invention is to use the neutralization and precipitation method to deeply remove arsenic and iron ions in the liquid after solid arsenic, and the obtained arsenic and iron salts are used for hydrothermal synthesis of scorodite. The neutralization precipitation method has the advantages of thorough removal of arsenic and iron salts and reuse of arsenic and iron salts.
本发明的第三个目的在于采用蒸发结晶法回收中和沉淀后液中的钠盐,实现溶液零排放处理。该方法具有钠盐结晶率高和钠盐产品成分稳定的优点。The third object of the present invention is to use evaporation crystallization method to recover the sodium salt in the liquid after neutralization and precipitation, so as to realize zero discharge treatment of the solution. This method has the advantages of high sodium salt crystallization rate and stable sodium salt product composition.
为达到上述目的,本发明提供如下的技术方案:将砷酸钠结晶物加入到蒸馏水中,缓慢滴加硫酸调节pH,然后转移至水热釜内加入固体三价铁源,在较高温度下保温并均匀搅拌,使砷铁沉淀结晶,沉淀物过滤、洗涤和干燥后即可得到稳定的片状臭葱石。采用中和沉淀法向固砷后液中加入氢氧化钠调节溶液pH,反应形成砷铁盐沉淀,并将该沉淀过滤、洗涤、干燥和细磨后用于合成臭葱石。将中和后液在高温连续蒸发再低温冷却结晶析出硫酸钠结晶产品,实现溶液的零排放目标。本发明的实质是利用高价砷、铁离子在高温溶液中易共沉淀为溶解度小且无毒的臭葱石晶体原理,实现砷酸钠中砷的无毒无害化。再利用砷铁离子水解沉淀为溶度积小的砷酸铁和氢氧化铁原理,完成固砷后液中残余砷铁的高效脱除。最后利用硫酸钠在过饱和溶液中可结晶析出的特性,实现中和后液蒸发结晶回收钠盐。In order to achieve the above object, the present invention provides the following technical solution: add sodium arsenate crystals to distilled water, slowly add sulfuric acid dropwise to adjust the pH, then transfer to a hydrothermal kettle and add a solid ferric iron source, and at a higher temperature Keep warm and stir evenly to precipitate and crystallize the iron arsenic. After filtering, washing and drying the precipitate, stable flaky scorodite can be obtained. The neutralization precipitation method is used to add sodium hydroxide to the post-arsenic solidification solution to adjust the pH of the solution. The reaction forms a precipitate of arsenic iron salt. The precipitate is filtered, washed, dried and finely ground for use in synthesizing scorodite. The neutralized liquid is continuously evaporated at high temperature and then cooled and crystallized at low temperature to precipitate the sodium sulfate crystal product to achieve the goal of zero discharge of the solution. The essence of the present invention is to utilize the principle that high-valent arsenic and iron ions are easy to co-precipitate into scorodite crystals with low solubility and non-toxicity in high-temperature solutions to achieve non-toxic and harmless arsenic in sodium arsenate. The principle of hydrolyzing and precipitating arsenic and iron ions into iron arsenate and iron hydroxide with small solubility products is then used to complete the efficient removal of residual arsenic and iron in the liquid after arsenic solidification. Finally, the characteristic that sodium sulfate can crystallize and precipitate in a supersaturated solution is used to realize the evaporation and crystallization of the neutralized liquid to recover the sodium salt.
为达到上述目的,本发明提供以下技术方案:In order to achieve the above objects, the present invention provides the following technical solutions:
(1)臭葱石晶体合成(1)Scorodite crystal synthesis
臭葱石晶体是砷酸钠结晶物先溶解为高砷酸性溶液,然后在该溶液中加入固体三价铁源高温水热结晶获得。取100g砷酸钠结晶物,按照液固比为(2~30):1加入蒸馏水,再按硫酸与砷酸钠结晶物质量比为1:(1.5~5)加入硫酸调节溶液pH=1~4。将该溶液加入到水热釜内,按铁砷摩尔比为(1~4):1加入固体三价铁盐,调控转速为200~600转/分钟,并升温至100~180℃,保温4~12小时,反应结束后冷却至室温,采用真空抽滤进行液、固分离。将固砷沉淀物和蒸馏水按质量比为1:(10~15)加入蒸馏水洗涤过滤,在60~85℃下干燥5~8小时后,即可得臭葱石晶体。合成的臭葱石晶体的毒性浸出性能满足中国国家标准(GB5085.3-2007)要求。上述过程中可能发生的化学反应为:Scorodite crystals are obtained by first dissolving sodium arsenate crystals into a high-arsenic acidic solution, and then adding a solid ferric iron source to the solution for high-temperature hydrothermal crystallization. Take 100g of sodium arsenate crystals, add distilled water according to the liquid-to-solid ratio of (2~30):1, and then add sulfuric acid to adjust the solution pH=1~ according to the mass ratio of sulfuric acid to sodium arsenate crystals of 1:(1.5~5). 4. Add the solution into the hydrothermal kettle, add solid ferric salt according to the molar ratio of iron to arsenic (1 to 4): 1, adjust the rotation speed to 200 to 600 rpm, and raise the temperature to 100 to 180°C, and keep it warm for 4 ~12 hours, after the reaction is completed, cool to room temperature, and use vacuum filtration to separate liquid and solid. Add the solid arsenic precipitate and distilled water at a mass ratio of 1: (10 to 15), add distilled water to wash and filter, and dry at 60 to 85°C for 5 to 8 hours to obtain scorodite crystals. The toxic leaching performance of the synthesized scorodite crystals meets the requirements of Chinese national standards (GB5085.3-2007). The chemical reactions that may occur during the above process are:
2Na3AsO4·12H2O+3H2SO4=3Na2SO4+2H3AsO4+24H2O (2)2Na 3 AsO 4 ·12H 2 O+3H 2 SO 4 =3Na 2 SO 4 +2H 3 AsO 4 +24H 2 O (2)
Fe(OH)3+3H+=Fe3++3H2O (3)Fe(OH) 3 +3H + =Fe 3+ +3H 2 O (3)
Fe2O3+6H+=2Fe3++3H2O (4)Fe 2 O 3 +6H + =2Fe 3+ +3H 2 O (4)
FeAsO4+nH+=Fe3++HnAsO4 (3-n)- (n=0,1,2,3) (5)FeAsO 4 +nH + =Fe 3+ +H n AsO 4 (3-n)- (n=0,1,2,3) (5)
Fe3++HnAsO4 (3-n)-+2H2O=FeAsO4·2H2O+nH+ (n=0,1,2,3) (6)Fe 3+ +H n AsO 4 (3-n)- +2H 2 O=FeAsO 4 ·2H 2 O+nH + (n=0,1,2,3) (6)
(2)中和沉淀除砷铁(2) Neutralization and precipitation of arsenic and iron
采用中和沉淀法向上述合成臭葱石产出的固砷后液中加入碱液,调节溶液pH,形成砷酸铁和氢氧化铁沉淀,实现除砷铁目标。量取固砷后液,滴加1~8mol/L的碱液,调节溶液初始pH=4~8,在室温下反应1~3小时。反应结束后真空抽滤、沉淀物和蒸馏水按质量比为1:(5-10)加蒸馏水洗涤过滤,在50~80℃干燥3~6小时后,干燥后的砷铁盐充分细磨过筛后,返回作为合成臭葱石晶体的铁盐,中和沉淀后液用于钠盐回收。上述过程可能发生的化学反应为:The neutralization precipitation method is used to add alkali solution to the arsenic solidification solution produced by the above-mentioned synthesis of scorodite, adjust the pH of the solution, and form iron arsenate and iron hydroxide precipitates to achieve the goal of arsenic and iron removal. Measure the arsenic solidification solution, add 1 to 8 mol/L alkali solution dropwise, adjust the initial pH of the solution to 4 to 8, and react at room temperature for 1 to 3 hours. After the reaction is completed, vacuum filtrate, add distilled water to the precipitate and distilled water at a mass ratio of 1:(5-10), wash and filter, dry at 50-80°C for 3-6 hours, and then the dried arsenic iron salt is fully finely ground and sieved. Afterwards, the iron salt is returned as the synthesized scorodite crystal, and the neutralized and precipitated liquid is used for sodium salt recovery. The chemical reactions that may occur in the above process are:
Fe3++3OH-=Fe(OH)3 (7)Fe 3+ +3OH - =Fe(OH) 3 (7)
Fe3++HnAsO4 (3-n)-=FeAsO4+nH+ (n=0,1,2,3) (8)Fe 3+ +H n AsO 4 (3-n)- =FeAsO 4 +nH + (n=0,1,2,3) (8)
Fe(OH)3+HnAsO4 (3-n)-+(3-n)H+=FeAsO4+3H2O (n=0,1,2,3) (9)Fe(OH) 3 +H n AsO 4 (3-n)- +(3-n)H + =FeAsO 4 +3H 2 O (n=0,1,2,3) (9)
H++OH-=H2O (10)H + +OH - =H 2 O (10)
(3)蒸发结晶回收钠盐(3) Evaporation and crystallization to recover sodium salt
将中和沉淀后液高温蒸发再低温冷却结晶,产出的结晶物为硫酸钠晶体产品。取上述中和沉淀后液加入至蒸发结晶器内,在120~160℃下连续浓缩4~10小时至料液比重在2~6g/cm3,再在5~10℃下冷却结晶5~12小时、真空抽滤、白色结晶物在60~80℃下干燥后,即可得到硫酸钠晶体产品。达到砷酸钠结晶物固化中溶液零排放目标。回收硫酸钠过程中发生的化学反应为:The neutralized and precipitated liquid is evaporated at high temperature and then cooled and crystallized at low temperature. The crystallized product is sodium sulfate crystal product. Add the above-mentioned neutralized and precipitated liquid into the evaporation crystallizer, continuously concentrate it at 120-160°C for 4-10 hours until the specific gravity of the material liquid is 2-6g/cm 3 , and then cool and crystallize it at 5-10°C for 5-12 hours. hour, vacuum filtration, and drying the white crystals at 60 to 80°C to obtain the sodium sulfate crystal product. Achieve the goal of zero discharge of solution during the solidification of sodium arsenate crystals. The chemical reactions that occur during the recovery of sodium sulfate are:
2Na++SO4 2-=Na2SO4(crystal) (11)2Na + +SO 4 2- =Na 2 SO 4(crystal) (11)
本发明中使用的富砷结晶物为锑冶炼中砷碱渣资源化利用中产生出的砷酸钠结晶物,其物相为Na3AsO4·xH2O(x=10,12),其中的主要化学成分(w.t.%)为Na14~26,As15~25,Sb 0.2~0.5,其余杂质为Ca,Cd,B≤0.10,结晶水为45~58。The arsenic-rich crystal used in the present invention is sodium arsenate crystal produced during the resource utilization of arsenic-alkali slag in antimony smelting, and its physical phase is Na 3 AsO 4 ·xH 2 O (x=10,12), where The main chemical components (wt%) are Na14~26, As15~25, Sb 0.2~0.5, the remaining impurities are Ca, Cd, B≤0.10, and the crystal water is 45~58.
本发明中固体三价铁盐为Fe(OH)3、Fe2O3、铁锈和中和沉淀回收的砷铁盐中一种或几种。In the present invention, the solid ferric salt is one or more of Fe(OH) 3 , Fe 2 O 3 , rust, and arsenic iron salt recovered by neutralization and precipitation.
本发明中使用的硫酸为分析纯试剂,其含量大于98%,碱液为分析纯的氢氧化钠,氢氧化钾,碳酸钠中的一种或几种溶解至水中获得。The sulfuric acid used in the present invention is an analytically pure reagent, and its content is greater than 98%. The alkali solution is obtained by dissolving one or more of analytically pure sodium hydroxide, potassium hydroxide, and sodium carbonate into water.
毒性浸出实验(TCLP),按照《固体废物浸出毒性浸出方法—硝酸硫酸法HJ/T299-2007》操作规范,将合成的臭葱石晶体材料按照液固比10:1加入到pH=3.15~3.25的硝酸硫酸混合水溶液中,水平震荡16~20小时,静置后上清液用0.8μm的滤膜过滤,毒性浸出液用ICP-AES测定砷浓度。按《危险废物鉴别标准—浸出毒性鉴别》(GB5085.3-2007)要求,当测定的毒性浸出液中砷浓度小于5mg/L,可认为合成的臭葱石晶体为无毒无害化材料,可长期安全储存。Toxicity leaching test (TCLP), in accordance with the operating specifications of "Solid Waste Leaching Toxicity Leaching Method—Nitric Acid Sulfuric Acid Method HJ/T299-2007", the synthesized scorodite crystal material was added to pH=3.15~3.25 according to the liquid-to-solid ratio of 10:1. In a mixed aqueous solution of nitric acid and sulfuric acid, shake horizontally for 16 to 20 hours. After standing, the supernatant is filtered with a 0.8 μm filter membrane. The arsenic concentration of the toxic leachate is measured by ICP-AES. According to the requirements of the "Hazardous Waste Identification Standard - Identification of Leaching Toxicity" (GB5085.3-2007), when the arsenic concentration in the measured toxic leachate is less than 5 mg/L, the synthesized scorodite crystals can be considered non-toxic and harmless materials. Safe long term storage.
本发明与传统从砷碱渣利用中富砷产物固化为臭葱石晶体方法相比较,具有如下优势:(1)固体三价铁盐的溶解消耗了臭葱石合成中释放的H+,消除了酸的累积,维持了溶液酸平衡和稳定化。(2)溶液反应前后pH变化小,提高了固砷效果,固砷率大于99.5%。(3)合成的臭葱石晶体为片状结构、发育完整,TCLP中砷浓度远远小于5mg/L,晶体结构稳定,适合于长期安全储存。(4)中和沉淀中铁砷去除率高(≥99.9%),砷铁盐可作为固体铁盐合成臭葱石,实现残余砷铁的利用。(5)蒸发结晶获得的硫酸钠产品中砷和铁含量低(<0.01%),适合作为其他化学品合成的原料。(6)整个富砷结晶物固化技术流程中,固砷后液、中和沉淀后液和结晶母液均无外排,杜绝了传统含砷废水排放对环境造成的污染。Compared with the traditional method of solidifying arsenic-rich products from arsenic-alkali residue into scorodite crystals, the present invention has the following advantages: (1) The dissolution of the solid ferric salt consumes the H + released during the synthesis of scorodite, eliminating the need for The accumulation of acid maintains the acid balance and stability of the solution. (2) The pH of the solution changes little before and after the reaction, which improves the arsenic fixation effect and the arsenic fixation rate is greater than 99.5%. (3) The synthesized scorodite crystals have a flaky structure and are fully developed. The arsenic concentration in TCLP is far less than 5 mg/L. The crystal structure is stable and suitable for long-term safe storage. (4) The removal rate of iron and arsenic in the neutralization precipitation is high (≥99.9%). The arsenic iron salt can be used as a solid iron salt to synthesize scorodite to realize the utilization of residual arsenic and iron. (5) The sodium sulfate product obtained by evaporation and crystallization has low arsenic and iron content (<0.01%) and is suitable as a raw material for the synthesis of other chemicals. (6) In the entire arsenic-rich crystal solidification technology process, the post-arsenic solidification liquid, post-neutralization precipitation liquid and crystallization mother liquor are not discharged, which eliminates the environmental pollution caused by traditional arsenic-containing wastewater discharge.
附图说明Description of the drawings
图1为本发明的工艺技术流程图;Figure 1 is a process technology flow chart of the present invention;
图2为本发明合成的臭葱石晶体的XRD图谱;Figure 2 is the XRD pattern of the scorodite crystal synthesized by the present invention;
图3为本发明合成的臭葱石晶体的SEM图;Figure 3 is an SEM image of the scorodite crystal synthesized by the present invention;
图4为本发明中和沉淀的砷铁盐的XRD图谱;Figure 4 is the XRD pattern of the neutralized and precipitated arsenic iron salt of the present invention;
图5为本发明中回收的硫酸钠晶体XRD图谱。Figure 5 is an XRD pattern of the sodium sulfate crystal recovered in the present invention.
具体实施方法Specific implementation methods
为使本发明实施例的目的、技术方案和优点更加清楚,下面将对本发明实施例中的技术方案进行清晰、完整地描述,显然,所描述的实施例是本发明一部分实施例,而不是全部的实施例。基于本发明中的实施例,本领域普通技术人员在没有做出创造性劳动前提下所获得的所有其他实施例,都属于本发明保护的范围。In order to make the purpose, technical solutions and advantages of the embodiments of the present invention clearer, the technical solutions in the embodiments of the present invention will be clearly and completely described below. Obviously, the described embodiments are part of the embodiments of the present invention, not all of them. Embodiments. Based on the embodiments of the present invention, all other embodiments obtained by those of ordinary skill in the art without creative efforts fall within the scope of protection of the present invention.
实施例1:Example 1:
称取100g砷酸钠结晶物,按液固比为30:1加入至3000mL的蒸馏水中,并按硫酸与砷酸钠结晶物质量比为1:2.5滴加硫酸调节溶液pH=2.0使砷酸钠完全溶解后得到含砷5g/L的酸性溶液。将该溶液加入至水热釜内,按铁砷摩尔比为2:1加入三氧化二铁固体铁盐,开启搅拌至300转/分钟,并升温至130℃,保温反应10小时,反应结束后冷却至室温,采用真空抽滤进行液、固分离。将固砷沉淀物和蒸馏水按质量比为1:10加入蒸馏水洗涤过滤,在65℃下干燥8小时后,即可得到臭葱石晶体,固砷率为99.60%。固砷后液的pH=2.02,基本接近初始pH,实现溶液中酸平衡和稳定化。向固砷后液中滴加5mol/L的氢氧化钠溶液调节溶液初始pH=4,在室温下反应1小时。反应结束后真空抽滤、沉淀物和蒸馏水按质量比为1:5加入蒸馏水洗涤过滤,在80℃干燥6小时后,产出的砷铁盐充分细磨过筛,作为合成臭葱石晶体的铁源。将中和沉淀后液加入至蒸发结晶器内,在120℃下连续浓缩6小时至料液比重在5g/cm3,再在5℃下冷却结晶10小时、真空抽滤、白色结晶物在60~80℃下干燥后即可得到硫酸钠晶体产品。Weigh 100g of sodium arsenate crystals, add them to 3000 mL of distilled water at a liquid-to-solid ratio of 30:1, and add sulfuric acid dropwise to adjust the pH of the solution to 2.0 according to a mass ratio of sulfuric acid to sodium arsenate crystals of 1:2.5 to make arsenic acid After the sodium is completely dissolved, an acidic solution containing 5g/L arsenic is obtained. Add the solution to the hydrothermal kettle, add ferric oxide solid iron salt according to the iron to arsenic molar ratio of 2:1, start stirring to 300 rpm, and raise the temperature to 130°C, keep the reaction for 10 hours, after the reaction is completed Cool to room temperature and use vacuum filtration to separate liquid and solid. Add the arsenic-solidified precipitate and distilled water to the distilled water at a mass ratio of 1:10, wash and filter, and dry at 65°C for 8 hours to obtain scorodite crystals with an arsenic-solidifying rate of 99.60%. The pH of the solution after arsenic solidification is 2.02, which is basically close to the initial pH, achieving acid balance and stabilization in the solution. Add 5 mol/L sodium hydroxide solution dropwise to the post-arsenic solidification solution to adjust the initial pH of the solution = 4, and react at room temperature for 1 hour. After the reaction is completed, vacuum filtration is carried out. The precipitate and distilled water are added to the distilled water at a mass ratio of 1:5, washed and filtered. After drying at 80°C for 6 hours, the produced arsenic iron salt is fully finely ground and sieved as the raw material for synthesizing scorodite crystals. Iron source. Add the neutralized and precipitated liquid into the evaporation crystallizer, continuously concentrate it at 120°C for 6 hours until the specific gravity of the material liquid is 5g/cm 3 , then cool and crystallize it at 5°C for 10 hours, vacuum filtrate, and remove the white crystals at 60 After drying at ~80°C, the sodium sulfate crystal product can be obtained.
实施例2:Example 2:
称取100g砷酸钠结晶物,按液固比为2.82:1加入至282mL的蒸馏水中,并按硫酸与砷酸钠结晶物质量比为1:2.92缓慢滴加硫酸调节溶液pH=2使砷酸钠溶解完全得到含砷50g/L的酸性溶液。将该溶液加入到水热釜内,按铁砷摩尔比为1.5:1加入固体三价铁盐(按回收的砷铁盐与氢氧化铁质量比2:1组成),调节搅拌为300转/分钟,并升温至120℃,保温反应8小时,反应结束后冷却至室温,真空抽滤进行液、固分离。将固砷沉淀物和蒸馏水按质量比为1:10加入蒸馏水洗涤过滤,在85℃下干燥8小时后,即可得到臭葱石晶体,固砷率为99.80%。固砷后液的pH=2.05,基本接近初始pH,实现溶液中酸平衡和稳定化。向固砷后液中滴加8mol/L的氢氧化钠溶液至初始pH=6.0,在室温下反应2小时。反应结束后真空抽滤、沉淀物和蒸馏水按质量比为1:6加入蒸馏水洗涤过滤,在80℃干燥6小时后,产出的砷铁盐充分细磨过筛,返回作为合成臭葱石晶体的铁盐。将中和沉淀后液加入到蒸发结晶器内,在140℃下连续浓缩6小时至料液比重在3g/cm3,再在5℃下冷却结晶8小时、真空抽滤、白色结晶物在60℃下干燥后即得硫酸钠晶体产品。Weigh 100g of sodium arsenate crystals, add them to 282 mL of distilled water at a liquid-to-solid ratio of 2.82:1, and slowly add sulfuric acid dropwise to adjust the pH of the solution to 2 at a mass ratio of sulfuric acid to sodium arsenate crystals of 1:2.92 to make the arsenic The sodium acid is completely dissolved to obtain an acidic solution containing 50g/L arsenic. Add the solution to the hydrothermal kettle, add solid ferric salt (based on the mass ratio of recovered arsenic iron salt and ferric hydroxide 2:1) according to the iron to arsenic molar ratio of 1.5:1, and adjust the stirring to 300 rpm/ minutes, and raise the temperature to 120°C, and keep the reaction for 8 hours. After the reaction is completed, it is cooled to room temperature, and vacuum filtration is performed to separate the liquid and solid. Add the arsenic-solidified precipitate and distilled water to the distilled water at a mass ratio of 1:10, wash and filter, and dry at 85°C for 8 hours to obtain scorodite crystals with an arsenic-solidifying rate of 99.80%. The pH of the solution after arsenic solidification is 2.05, which is basically close to the initial pH, achieving acid balance and stabilization in the solution. Add 8mol/L sodium hydroxide solution dropwise to the arsenic solidification solution until the initial pH=6.0, and react at room temperature for 2 hours. After the reaction is completed, the precipitate and distilled water are washed and filtered by adding distilled water at a mass ratio of 1:6. After drying at 80°C for 6 hours, the produced arsenic iron salt is fully finely ground and sieved, and returned as synthetic scorodite crystals. of iron salt. Add the neutralized and precipitated liquid into the evaporation crystallizer, continuously concentrate it at 140°C for 6 hours until the specific gravity of the material liquid is 3g/cm 3 , then cool and crystallize it at 5°C for 8 hours, vacuum filtrate, and the white crystals are collected at 60 After drying at ℃, the sodium sulfate crystal product is obtained.
实施例3:Example 3:
称取100g砷酸钠结晶物,按液固比为2:1加入至200mL的蒸馏水中,按硫酸与砷酸钠结晶物质量比为1:2.18加入硫酸调节溶液pH=1,使砷酸钠溶解完全得到含砷70g/L的酸性溶液。将该溶液加入到水热釜内,按照铁砷摩尔比为1.8:1加入氢氧化铁,调节转速至400转/分钟,并升温至150℃,保温反应12小时,反应结束后冷却至室温,真空抽滤进行液、固分离。将固砷沉淀物和蒸馏水按质量比为1:15加入蒸馏水洗涤,过滤,在80℃下干燥6小时后,即可得到臭葱石晶体,固砷率为99.5%。固砷后液的pH=1.04,基本接近初始pH,实现溶液中酸平衡和稳定化。向固砷后液中滴加4mol/L的碱性溶液调节溶液初始pH=7.0,在室温下反应3小时。反应结束后真空抽滤、沉淀物和蒸馏水按质量比为1:5加蒸馏水洗涤过滤,在80℃干燥4小时,产出的砷铁盐充分细磨过筛后,返回作为合成臭葱石晶体的铁盐。将产生的中和沉淀后液加入至蒸发结晶器内,在120℃下连续浓缩4小时至料液比重在2.5g/cm3,再在8℃下冷却结晶7小时、真空抽滤、白色结晶物在80℃下干燥后即可得到硫酸钠晶体产品。Weigh 100g of sodium arsenate crystals, add to 200 mL of distilled water at a liquid-to-solid ratio of 2:1, add sulfuric acid at a mass ratio of sulfuric acid to sodium arsenate crystals of 1:2.18 to adjust the pH of the solution = 1, so that sodium arsenate Dissolve completely to obtain an acidic solution containing 70g/L arsenic. Add the solution to the hydrothermal kettle, add iron hydroxide according to the iron to arsenic molar ratio of 1.8:1, adjust the rotation speed to 400 rpm, and raise the temperature to 150°C, keep the reaction for 12 hours, and cool to room temperature after the reaction is completed. Vacuum filtration is used to separate liquid and solid. Add the arsenic-solidified precipitate and distilled water at a mass ratio of 1:15, add distilled water for washing, filter, and dry at 80°C for 6 hours to obtain scorodite crystals with an arsenic-solidifying rate of 99.5%. The pH of the solution after arsenic solidification is 1.04, which is basically close to the initial pH, achieving acid balance and stabilization in the solution. Add 4 mol/L alkaline solution dropwise to the post-arsenic solidification solution to adjust the initial pH of the solution = 7.0, and react at room temperature for 3 hours. After the reaction is completed, vacuum filtrate, add distilled water to the precipitate and distilled water at a mass ratio of 1:5, wash and filter, and dry at 80°C for 4 hours. The produced arsenic iron salt is fully finely ground and sieved, and then returned as synthetic scorodite crystals. of iron salt. Add the neutralized and precipitated liquid to the evaporation crystallizer, continuously concentrate it at 120°C for 4 hours until the specific gravity of the material liquid is 2.5g/cm 3 , then cool and crystallize at 8°C for 7 hours, vacuum filtrate, and white crystallize. After drying the material at 80°C, the sodium sulfate crystal product can be obtained.
以上合成的臭葱石晶体均按照《固体废物浸出毒性浸出方法—硝酸硫酸法HJ/T299-2007》操作规范浸出毒性浸出实验,毒性浸出液采用ICP-AES测定,砷浓度均低于5mg/L,是无毒无害的固砷材料,适合安全储存。The scorodite crystals synthesized above were leached for toxicity leaching experiments in accordance with the "Solid Waste Leaching Toxicity Leaching Method - Nitric Acid Sulfuric Acid Method HJ/T299-2007" operating specifications. The toxicity leachate was measured by ICP-AES, and the arsenic concentrations were all lower than 5mg/L. It is a non-toxic and harmless arsenic-fixing material, suitable for safe storage.
图1为本发明的技术流程图,本技术是由水热固化、中和沉淀和蒸发结晶三道关键工序组成,富砷结晶物分别转化为臭葱石晶体、砷铁盐和硫酸钠晶体。其中臭葱石是无毒材料,适合安全储存;砷铁盐返回水热固化合成臭葱石,实现铁砷循环;过程中产生的固砷后液、中和后液和结晶母液实行闭路处理。这三道工序紧密相联,共同构成砷碱渣资源化利用中富砷结晶物的无毒无害化技术。Figure 1 is a technical flow chart of the present invention. This technology consists of three key processes: hydrothermal solidification, neutralization precipitation and evaporation crystallization. Arsenic-rich crystals are converted into scorodite crystals, arsenic iron salts and sodium sulfate crystals respectively. Among them, scorodite is a non-toxic material and is suitable for safe storage; the arsenic iron salt is returned to hydrothermal solidification to synthesize scorodite to realize iron and arsenic circulation; the post-arsenic liquid, post-neutralization liquid and crystallization mother liquor produced in the process are processed in a closed circuit. These three processes are closely linked and together constitute a non-toxic and harmless technology for arsenic-rich crystallization in the resource utilization of arsenic-alkali slag.
图2表明,水热固化合成的臭葱石晶体为衍射峰尖锐的FeAsO4·2H2O相,在2θ=15.78°,19.82°,28.04°,29.16°,和35.82°处分别对应(1 1 1),(2 0 0),(2 1 2),(1 31),和(3 2 0)晶面,说明合成的臭葱石晶体为结晶性良好。图3表明合成的臭葱石为粒径在5—10μm的片状结构,这些片状结构紧密排列,晶体发育完全。Figure 2 shows that the scorodite crystal synthesized by hydrothermal solidification is a FeAsO 4 ·2H 2 O phase with sharp diffraction peaks, corresponding to (1 1 1), (2 0 0), (2 1 2), (1 31), and (3 2 0) crystal planes, indicating that the synthesized scorodite crystal has good crystallinity. Figure 3 shows that the synthesized scorodite has a flaky structure with a particle size of 5-10 μm. These flaky structures are closely arranged and the crystals are fully developed.
图4表明中和沉淀回收的砷铁盐为无定形物相,XRD图谱中仅在2θ=10~20°,25~40°和50~65°三处较宽的范围的衍射角度内存在弱结晶峰,与FeAsO4和Fe(OH)3的标准图谱匹配度较低,说明在中和沉淀法产生的砷铁盐为无定形结构。图5表明蒸发结晶后获得硫酸钠晶体的物相组成单一、衍射峰尖锐,与Na2SO4标准PDF卡匹配度高,说明硫酸钠晶体结晶性良好。Figure 4 shows that the arsenic iron salt recovered by neutralization precipitation is an amorphous phase. In the XRD pattern, there are only weak diffraction angles in three wide ranges of 2θ=10~20°, 25~40° and 50~65°. The crystallization peak has a low matching degree with the standard spectra of FeAsO 4 and Fe(OH) 3 , indicating that the arsenic iron salt produced by the neutralization precipitation method has an amorphous structure. Figure 5 shows that the sodium sulfate crystal obtained after evaporation and crystallization has a single phase composition, sharp diffraction peaks, and a high degree of matching with the Na 2 SO 4 standard PDF card, indicating that the sodium sulfate crystal has good crystallinity.
综上所述,本发明提出的水热固化法能将砷碱渣资源化利用中富砷结晶物转化为无毒无害的片状臭葱石晶体固砷材料。固体三价铁盐能中和合成中释放的氢离子,实现溶液酸平衡和稳定化。无含砷固废和废水排放,达到砷碱渣中砷安全化处理和环境保护。In summary, the hydrothermal solidification method proposed in the present invention can convert arsenic-rich crystals used in the resource utilization of arsenic-alkali residue into non-toxic and harmless flaky scorodite crystal arsenic-fixing materials. Solid ferric salt can neutralize the hydrogen ions released during synthesis to achieve acid balance and stabilization of the solution. There is no arsenic-containing solid waste and wastewater discharge, achieving safe treatment of arsenic in arsenic-alkali residue and environmental protection.
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Citations (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102674526A (en) * | 2012-05-14 | 2012-09-19 | 中南大学 | Method for precipitating and stabilizing As from As-containing solution |
| WO2013173914A1 (en) * | 2012-05-25 | 2013-11-28 | The University Of British Columbia | Arsenic recovery from copper-arsenic sulphides |
| CN108455679A (en) * | 2018-05-17 | 2018-08-28 | 中南大学 | A kind of preparation method and applications of three-dimensional globular scorodite crystals |
| JP2018150186A (en) * | 2017-03-11 | 2018-09-27 | 三菱マテリアル株式会社 | Method for producing scorodite |
| CN110801802A (en) * | 2019-11-20 | 2020-02-18 | 中南大学 | Scorodite arsenic fixing material and preparation method thereof |
| CN111039327A (en) * | 2019-12-31 | 2020-04-21 | 福州大学 | Method for converting arsenic slag into scorodite in one step |
| CN111170510A (en) * | 2020-01-20 | 2020-05-19 | 宁波弗镁瑞环保科技有限公司 | A method for treating and solidifying arsenic in wastewater containing arsenic |
| CN111620380A (en) * | 2020-07-10 | 2020-09-04 | 中南大学 | Method for preparing scorodite by hydrothermally treating trivalent arsenic and application thereof |
| CN114561558A (en) * | 2022-02-23 | 2022-05-31 | 中南大学 | A method for recovering antimony and solid arsenic from arsenic-containing crystals |
Family Cites Families (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP4538481B2 (en) * | 2007-09-25 | 2010-09-08 | 日鉱金属株式会社 | Method for producing scorodite and method for recycling liquid after synthesis of scorodite |
| FI122349B (en) * | 2009-02-23 | 2011-12-15 | Outotec Oyj | Procedure for removing arsenic as chorodite |
-
2022
- 2022-09-14 CN CN202211119098.3A patent/CN115304105B/en active Active
Patent Citations (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102674526A (en) * | 2012-05-14 | 2012-09-19 | 中南大学 | Method for precipitating and stabilizing As from As-containing solution |
| WO2013173914A1 (en) * | 2012-05-25 | 2013-11-28 | The University Of British Columbia | Arsenic recovery from copper-arsenic sulphides |
| JP2018150186A (en) * | 2017-03-11 | 2018-09-27 | 三菱マテリアル株式会社 | Method for producing scorodite |
| CN108455679A (en) * | 2018-05-17 | 2018-08-28 | 中南大学 | A kind of preparation method and applications of three-dimensional globular scorodite crystals |
| CN110801802A (en) * | 2019-11-20 | 2020-02-18 | 中南大学 | Scorodite arsenic fixing material and preparation method thereof |
| CN111039327A (en) * | 2019-12-31 | 2020-04-21 | 福州大学 | Method for converting arsenic slag into scorodite in one step |
| CN111170510A (en) * | 2020-01-20 | 2020-05-19 | 宁波弗镁瑞环保科技有限公司 | A method for treating and solidifying arsenic in wastewater containing arsenic |
| CN111620380A (en) * | 2020-07-10 | 2020-09-04 | 中南大学 | Method for preparing scorodite by hydrothermally treating trivalent arsenic and application thereof |
| CN114561558A (en) * | 2022-02-23 | 2022-05-31 | 中南大学 | A method for recovering antimony and solid arsenic from arsenic-containing crystals |
Non-Patent Citations (4)
| Title |
|---|
| A novel process of immobilizing sodium arsenate crystals as scorodite using Fe(OH)3 as an iron source;Zanlang Tang等;《Process Safety and Environmental Protection 》;第1-15页 * |
| Hydrothermal reaction chemistry and characterization of ferric arsenate phases precipitated from Fe2(SO4)3–As2O5–H2SO4 solutions;M.A. Gomez等;《Hydrometallurgy》;第74–90页 * |
| 含砷铁溶液水热臭葱石沉砷研究;余自秀等;《昆明理工大学学报(自然科学版)》;第1-8页 * |
| 钠离子对水热臭葱石沉砷过程影响及亚稳态铁物相转变行为;张鹏;李存兄;魏昶;楚铭;张俊;;中国有色金属学报(05);第207-217页 * |
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