CN117025985B - A method and application of recovering rare earth elements from red mud using acidophilic thermophilic red algae - Google Patents

A method and application of recovering rare earth elements from red mud using acidophilic thermophilic red algae Download PDF

Info

Publication number
CN117025985B
CN117025985B CN202311022382.3A CN202311022382A CN117025985B CN 117025985 B CN117025985 B CN 117025985B CN 202311022382 A CN202311022382 A CN 202311022382A CN 117025985 B CN117025985 B CN 117025985B
Authority
CN
China
Prior art keywords
red
rare earth
red mud
earth elements
algae
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.)
Active
Application number
CN202311022382.3A
Other languages
Chinese (zh)
Other versions
CN117025985A (en
Inventor
王志斌
张熙如
刘文佳
郭志伟
巩春容
余志晟
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
University of Chinese Academy of Sciences
Original Assignee
University of Chinese Academy of Sciences
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by University of Chinese Academy of Sciences filed Critical University of Chinese Academy of Sciences
Priority to CN202311022382.3A priority Critical patent/CN117025985B/en
Publication of CN117025985A publication Critical patent/CN117025985A/en
Application granted granted Critical
Publication of CN117025985B publication Critical patent/CN117025985B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B59/00Obtaining rare earth metals
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B3/00Extraction of metal compounds from ores or concentrates by wet processes
    • C22B3/18Extraction of metal compounds from ores or concentrates by wet processes with the aid of microorganisms or enzymes, e.g. bacteria or algae
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B7/00Working up raw materials other than ores, e.g. scrap, to produce non-ferrous metals and compounds thereof; Methods of a general interest or applied to the winning of more than two metals
    • C22B7/006Wet processes
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling

Landscapes

  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Mechanical Engineering (AREA)
  • Organic Chemistry (AREA)
  • Manufacturing & Machinery (AREA)
  • General Life Sciences & Earth Sciences (AREA)
  • Materials Engineering (AREA)
  • Environmental & Geological Engineering (AREA)
  • Metallurgy (AREA)
  • Geology (AREA)
  • Biochemistry (AREA)
  • Biotechnology (AREA)
  • Microbiology (AREA)
  • Geochemistry & Mineralogy (AREA)
  • Micro-Organisms Or Cultivation Processes Thereof (AREA)
  • Manufacture And Refinement Of Metals (AREA)

Abstract

The invention provides a method for recycling rare earth elements from red mud by utilizing acidophilic thermophilic red algae and application thereof, and belongs to the technical field of resource recycling. The method comprises the steps of mixing red mud leaching liquor, acidophilic thermophilic red algae seed liquor and a carbon source to obtain a treatment liquor to be recovered; and recycling the rare earth elements in the treatment liquid to be recycled by utilizing acidophilic thermophilic red algae, wherein the unicellular acidophilic thermophilic red algae is G.sulfophiaria. Compared with other microalgae recovery technologies, the method for recovering the rare earth elements in the red mud can effectively avoid the pollution and interference of mixed bacteria, and simultaneously avoid complicated sterilization procedures. The method of the invention has the advantages of easy implementation, high treatment efficiency, good absorption effect, low cost and environmental protection.

Description

一种利用嗜酸嗜热红藻从赤泥中回收稀土元素的方法及应用A method and application of recovering rare earth elements from red mud using acidophilic thermophilic red algae

技术领域Technical Field

本发明属于资源回收利用技术领域,尤其涉及一种利用嗜酸嗜热红藻从赤泥中回收稀土元素的方法及应用。The invention belongs to the technical field of resource recycling, and in particular relates to a method and application of recycling rare earth elements from red mud by utilizing acidophilic thermophilic red algae.

背景技术Background technique

赤泥是从铝土矿中提取氧化铝后排放的固体废弃物,研究表明,平均每生产1吨氧化铝大约产生1-2吨赤泥,全世界每年赤泥产生量在1.5亿吨左右。我国氧化铝产量超过2500万吨,赤泥产量超过4000万吨,但赤泥的综合利用率仅为4%,而赤泥的累积堆存量已经超过2亿吨。一方面,赤泥的大量堆放不仅占用大量土地,堆场的建设和维护消耗大量资金,存放不当,容易引发污染土壤、地下水和大气污染,进而恶化生态环境;另一方面,赤泥中含有大量的可再生利用金属元素,特别是含有丰富的有价金属,如铁、铝、钙、钛、稀土等金属元素。稀土元素被认为是很多高科技材料的关键重要金属,有工业“黄金”之称,在新能源、冶金、石油化工、玻璃陶瓷、航空航天等领域有着广泛的应用,因此对稀土元素的需求正在持续增长。因此,从赤泥中回收稀土金属不仅可实现资源的回收利用,更有助于减少环境污染、助力生态文明建设。Red mud is a solid waste discharged after alumina is extracted from bauxite. Studies have shown that on average, about 1-2 tons of red mud are produced for every ton of alumina produced, and the annual red mud production in the world is about 150 million tons. my country's alumina production exceeds 25 million tons, and red mud production exceeds 40 million tons, but the comprehensive utilization rate of red mud is only 4%, and the cumulative stockpile of red mud has exceeded 200 million tons. On the one hand, the large-scale stacking of red mud not only occupies a large amount of land, but also consumes a lot of money in the construction and maintenance of the yard. Improper storage can easily cause soil, groundwater and air pollution, and thus deteriorate the ecological environment; on the other hand, red mud contains a large amount of renewable metal elements, especially rich in valuable metals, such as iron, aluminum, calcium, titanium, rare earth and other metal elements. Rare earth elements are considered to be the key and important metals of many high-tech materials. They are known as industrial "gold" and are widely used in new energy, metallurgy, petrochemicals, glass and ceramics, aerospace and other fields. Therefore, the demand for rare earth elements is continuing to grow. Therefore, recovering rare earth metals from red mud can not only achieve resource recycling, but also help reduce environmental pollution and promote the construction of ecological civilization.

目前,从赤泥中回收稀土元素的方法主要是采用三种工艺,一种是直接用无机酸浸出赤泥中的稀土元素,使铈、钙、钛等元素生成可溶性盐,属于强酸浸出过程,该过程存在酸用量大,分离步骤复杂的问题;第二种是硫酸化焙烧赤泥后浸出稀土元素,该方法硫酸浓度高,且硫酸酸化过程涉及的焙烧温度高;第三种是物理分选与化学溶出结合的手段,如通过还原焙烧-磁选除铁、酸浸除硅、氢氧化钠溶液浸出除铝得到稀土元素。但是,无论采用哪种工艺,均面临高能耗和高酸碱带来的高碳排放和环境污染问题。At present, there are mainly three methods for recovering rare earth elements from red mud. One is to directly leach rare earth elements from red mud with inorganic acid to generate soluble salts of elements such as cerium, calcium, and titanium. This is a strong acid leaching process, which has the problems of large acid dosage and complicated separation steps. The second is to leach rare earth elements after sulphate roasting of red mud. This method has high sulfuric acid concentration and high roasting temperature involved in the sulphuric acid acidification process. The third is a combination of physical separation and chemical dissolution, such as reducing roasting-magnetic separation to remove iron, acid leaching to remove silicon, and sodium hydroxide solution leaching to remove aluminum to obtain rare earth elements. However, no matter which process is used, it faces the problems of high carbon emissions and environmental pollution caused by high energy consumption and high acid and alkali.

近年来,利用生物技术进行环境和废水生物修复因其成本低、低碳环保、品种多、性能优异而受到越来越多的关注。在这种情况下,利用藻类回收液相中的稀土元素就成为潜在的生物技术手段。早在1997年,Hao等人(1997)研究了活小球藻富集稀土元素的过程。2002年,Palmieri等利用干燥的马尾藻(Sargassum fluitans)去除La3+。2017年,Jacinto等首次报道了活的大型藻类可以去除和回收稀土。虽然藻类有潜力为稀土的去除提供可持续的材料,但其高效性、可控性及回收过程的便利化仍需大幅提升。特别是现有多数生物无法适应赤泥提取物的低pH和高浓度的金属环境,因此,制约了藻类从赤泥中回收稀土元素技术的应用与推广。In recent years, the use of biotechnology for environmental and wastewater bioremediation has attracted increasing attention due to its low cost, low carbon and environmental protection, wide variety and excellent performance. In this context, the use of algae to recover rare earth elements in the liquid phase has become a potential biotechnology method. As early as 1997, Hao et al. (1997) studied the process of rare earth element enrichment by living Chlorella. In 2002, Palmieri et al. used dried Sargassum fluitans to remove La 3+ . In 2017, Jacinto et al. first reported that living macroalgae can remove and recover rare earths. Although algae have the potential to provide sustainable materials for the removal of rare earths, their efficiency, controllability and convenience of the recovery process still need to be greatly improved. In particular, most existing organisms cannot adapt to the low pH and high metal concentration environment of red mud extracts, which restricts the application and promotion of algae technology for recovering rare earth elements from red mud.

发明内容Summary of the invention

为解决上述技术问题,本发明提出了一种利用嗜酸嗜热红藻从赤泥中回收稀土元素的方法及应用,利用嗜酸嗜热微藻能够在极端环境中生存的特点,令其在赤泥酸浸废水中生存,同时吸收其中的稀土元素,从而实现稀土金属元素的回收和二次利用。In order to solve the above technical problems, the present invention proposes a method and application of recovering rare earth elements from red mud by using acidophilic thermophilic red algae. The method utilizes the ability of acidophilic thermophilic microalgae to survive in extreme environments, allowing them to survive in red mud acid leaching wastewater and absorb the rare earth elements therein, thereby realizing the recovery and secondary utilization of rare earth metal elements.

本发明提出了一种利用嗜酸嗜热红藻从赤泥中回收稀土元素的方法,将赤泥浸提液与嗜酸嗜热红藻种液混合得到待回收处理液,回收培养,利用嗜酸嗜热红藻对待回收处理液进行净化,实现赤泥中稀土元素的回收,所述嗜酸嗜热红藻种液为富含单细胞红藻G.sulphuraria的藻液,藻种编号为G.sulphuraria UTEX 2919,本发明发现其能够在酸性热硫磺泉、硫气孔、露天矿山以及内生岩等不利的生态环境中生存,可耐受高温(高达63℃)、强酸(pH为0-4.0)、高渗透压(9%的盐度)和高浓度重金属(如铬、镍)等多种极端环境,且对重金属等具有良好的吸附性,无需修饰或预处理,即可作为重金属生物吸附剂,具有大规模生产的潜力。The present invention proposes a method for recovering rare earth elements from red mud by using acidophilic thermophilic red algae. The method comprises the following steps: mixing red mud extract with acidophilic thermophilic red algae seed liquid to obtain a to-be-recovered treatment liquid, recovering and culturing the mixture, and purifying the to-be-recovered treatment liquid by using the acidophilic thermophilic red algae to recover rare earth elements from the red mud. The acidophilic thermophilic red algae seed liquid is an algae liquid rich in unicellular red algae G. sulphuraria, and the algae species number is G. sulphuraria UTEX 2919. The present invention finds that the acidophilic thermophilic red algae can survive in adverse ecological environments such as acidic hot sulfur springs, sulfur pores, open-pit mines, and endogenous rocks, and can withstand a variety of extreme environments such as high temperature (up to 63° C.), strong acid (pH of 0-4.0), high osmotic pressure (9% salinity), and high concentration of heavy metals (such as chromium and nickel). The acidophilic thermophilic red algae seed liquid has good adsorption properties for heavy metals and the like, and can be used as a heavy metal biosorbent without modification or pretreatment, and has the potential for large-scale production.

进一步地,包括以下步骤:将赤泥与提取液混合,振荡、离心,取上清液,得到赤泥浸提液,将所述赤泥浸提液、嗜酸嗜热红藻种液和碳源混合,得到待回收处理液,将所述待回收处理液进行回收培养,离心沉降分离吸附有稀土元素的嗜酸嗜热红藻,用去离子水冲洗2-3遍,加入解吸附剂,振荡,实现赤泥中稀土元素的富集和回收。Furthermore, the method comprises the following steps: mixing red mud with an extract, oscillating and centrifuging, taking a supernatant to obtain a red mud extract, mixing the red mud extract, an acidophilic and thermophilic red algae seed solution and a carbon source to obtain a treated liquid to be recovered, recovering and culturing the treated liquid to be recovered, separating the acidophilic and thermophilic red algae adsorbed with rare earth elements by centrifugal sedimentation, rinsing with deionized water for 2-3 times, adding a desorbent, and oscillating to achieve the enrichment and recovery of rare earth elements in red mud.

进一步地,所述解吸附剂为浓度0.1mol/L的HNO3Furthermore, the desorbent is HNO 3 with a concentration of 0.1 mol/L.

进一步地,所述嗜酸嗜热红藻种液制备方法为:在室温下,将单细胞红藻G.sulphuraria接种于盛有BG11培养基的锥形瓶中进行预培养,初始接种浓度为0.44g/L,培养时间为7天,光照强度为2500lx,光暗比12h∶12h,得到嗜酸嗜热红藻种液。Furthermore, the method for preparing the acidophilic thermophilic red algae seed solution is as follows: at room temperature, the unicellular red algae G. sulphuraria is inoculated into a conical flask containing BG11 culture medium for pre-culture, the initial inoculation concentration is 0.44 g/L, the culture time is 7 days, the light intensity is 2500 lx, and the light-dark ratio is 12h:12h, to obtain the acidophilic thermophilic red algae seed solution.

进一步地,所述提取液为体积分数为10%的硝酸溶液,赤泥与提取液的固液比为1kg∶50L。Furthermore, the extract is a nitric acid solution with a volume fraction of 10%, and the solid-liquid ratio of red mud to the extract is 1kg:50L.

进一步地,在室温下振荡10h后,在2000g条件下离心10min。Furthermore, after shaking at room temperature for 10 h, the mixture was centrifuged at 2000 g for 10 min.

进一步地,所述待回收处理液中,赤泥浸提液的体积为10%。Furthermore, in the treated liquid to be recovered, the volume of red mud extract is 10%.

进一步地,所述碳源包括甘油或葡萄糖中的一种或两种,碳源在待回收处理液中的添加量为20-40g/L。Furthermore, the carbon source includes one or both of glycerol and glucose, and the amount of the carbon source added to the treated liquid to be recovered is 20-40 g/L.

进一步地,所述待回收处理液中,嗜酸嗜热红藻初始细胞密度为1.8×106cells/mL。Furthermore, in the treated liquid to be recovered, the initial cell density of the acidophilic and thermophilic red algae is 1.8×10 6 cells/mL.

进一步地,所述回收培养的温度为40℃,湿度为50~70%,时间为5-10d,pH为2.5~4,优选,pH为3.5。Furthermore, the recovery culture is carried out at a temperature of 40° C., a humidity of 50-70%, a time of 5-10 days, a pH of 2.5-4, and preferably a pH of 3.5.

进一步地,所述回收培养在光照(全光谱LED灯)下进行,光照强度为8000~12000Lx,光暗周期比为16h:8h。Furthermore, the recovery culture is carried out under illumination (full-spectrum LED light), the illumination intensity is 8000-12000Lx, and the light-dark cycle ratio is 16h:8h.

本发明还提出了上述方法在赤泥回收处理中的应用。The invention also proposes the application of the method in red mud recovery and treatment.

与现有技术相比,本发明具有如下优点和技术效果:Compared with the prior art, the present invention has the following advantages and technical effects:

本发明利用单细胞嗜酸嗜热红藻对稀土元素特有的吸收性能,可以实现赤泥中稀土元素的快速吸收。采用本发明提供的方法回收赤泥中的稀土元素,由于该方法中pH在2.5~4,温度在40℃,相比于其他微藻回收技术,能够有效避免杂菌的污染和干扰,同时避免了繁杂的灭菌程序。本发明的方法易实施、处理效率高、吸收效果好,且还具有成本低、绿色环保的特点。The present invention utilizes the unique absorption performance of single-cell acidophilic thermophilic red algae for rare earth elements, and can achieve rapid absorption of rare earth elements in red mud. The method provided by the present invention is used to recover rare earth elements in red mud. Since the pH in the method is 2.5-4 and the temperature is 40°C, compared with other microalgae recovery technologies, it can effectively avoid contamination and interference from miscellaneous bacteria, and at the same time avoid complicated sterilization procedures. The method of the present invention is easy to implement, has high processing efficiency, good absorption effect, and is also low-cost and green and environmentally friendly.

附图说明BRIEF DESCRIPTION OF THE DRAWINGS

构成本申请的一部分的附图用来提供对本申请的进一步理解,本申请的示意性实施例及其说明用于解释本申请,并不构成对本申请的不当限定。在附图中:The drawings constituting a part of the present application are used to provide a further understanding of the present application. The illustrative embodiments and descriptions of the present application are used to explain the present application and do not constitute an improper limitation on the present application. In the drawings:

图1为单细胞红藻G.sulphuraria的光学图片;Figure 1 is an optical picture of the unicellular red alga G. sulphuraria;

图2为G.sulphuraria在对照组和RM组中培养得到的生长曲线;FIG2 is a growth curve of G. sulphuraria cultured in the control group and the RM group;

图3为实施例1-4不同pH下细胞中总稀土元素含量测定结果;FIG3 is the results of measuring the total rare earth element content in cells at different pH values in Examples 1-4;

图4为实施例5(RM)与对比例1(control)吸收富集的单一稀土元素的浓度结果;FIG4 is the concentration results of a single rare earth element absorbed and enriched in Example 5 (RM) and Comparative Example 1 (control);

图5为实施例5(RM)与对比例1(对照)吸收富集的总稀土元素浓度结果;FIG5 is the results of total rare earth element concentrations absorbed and enriched by Example 5 (RM) and Comparative Example 1 (control);

图6为实施例3、实施例5、实施例6以及对比例2-4中G.sulphuraria累积的总稀土元素浓度结果。FIG6 shows the total rare earth element concentration results accumulated by G. sulphuraria in Example 3, Example 5, Example 6 and Comparative Examples 2-4.

具体实施方式Detailed ways

现详细说明本发明的多种示例性实施方式,该详细说明不应认为是对本发明的限制,而应理解为是对本发明的某些方面、特性和实施方案的更详细的描述。Various exemplary embodiments of the present invention will now be described in detail. This detailed description should not be considered as limiting the present invention, but should be understood as a more detailed description of certain aspects, features, and embodiments of the present invention.

应理解本发明中所述的术语仅仅是为描述特别的实施方式,并非用于限制本发明。另外,对于本发明中的数值范围,应理解为还具体公开了该范围的上限和下限之间的每个中间值。在任何陈述值或陈述范围内的中间值以及任何其他陈述值或在所述范围内的中间值之间的每个较小的范围也包括在本发明内。这些较小范围的上限和下限可独立地包括或排除在范围内。It should be understood that the terms described in the present invention are only for describing a particular embodiment and are not intended to limit the present invention. In addition, for the numerical range in the present invention, it should be understood that each intermediate value between the upper and lower limits of the scope is also specifically disclosed. Each smaller range between the intermediate value in any stated value or stated range and any other stated value or intermediate value in the described range is also included in the present invention. The upper and lower limits of these smaller ranges can be independently included or excluded in the scope.

除非另有说明,否则本文使用的所有技术和科学术语具有本发明所述领域的常规技术人员通常理解的相同含义。虽然本发明仅描述了优选的方法和材料,但是在本发明的实施或测试中也可以使用与本文所述相似或等同的任何方法和材料。本说明书中提到的所有文献通过引用并入,用以公开和描述与所述文献相关的方法和/或材料。在与任何并入的文献冲突时,以本说明书的内容为准。Unless otherwise indicated, all technical and scientific terms used herein have the same meanings as those generally understood by those skilled in the art. Although the present invention describes only preferred methods and materials, any methods and materials similar or equivalent to those described herein may also be used in the implementation or testing of the present invention. All documents mentioned in this specification are incorporated by reference to disclose and describe the methods and/or materials associated with the documents. In the event of a conflict with any incorporated document, the content of this specification shall prevail.

在不背离本发明的范围或精神的情况下,可对本发明说明书的具体实施方式做多种改进和变化,这对本领域技术人员而言是显而易见的。由本发明的说明书得到的其他实施方式对技术人员而言是显而易见得的。本发明说明书和实施例仅是示例性的。It will be apparent to those skilled in the art that various modifications and variations may be made to the specific embodiments of the present invention description without departing from the scope or spirit of the present invention. Other embodiments derived from the present invention description will be apparent to those skilled in the art. The present invention description and examples are exemplary only.

关于本文中所使用的“包含”、“包括”、“具有”、“含有”等等,均为开放性的用语,即意指包含但不限于。The words “include,” “including,” “have,” “contain,” etc. used in this document are open-ended terms, meaning including but not limited to.

本发明提出了一种利用嗜酸嗜热红藻从赤泥中回收稀土元素的方法,将赤泥浸提液与嗜酸嗜热红藻种液混合,回收培养,实现赤泥中稀土元素的回收,所述嗜酸嗜热红藻种液为富含单细胞红藻G.sulphuraria的藻液,藻种编号为G.sulphuraria UTEX 2919,购于美国德克萨斯州大学藻种库(UTEX),光学图片见图1,其能够在酸性热硫磺泉、硫气孔、露天矿山以及内生岩等不利的生态环境中生存,可耐受高温(高达63℃)、强酸(pH 0-4.0)、高渗透压(9%的盐度)和高浓度重金属(如铬、镍)等多种极端环境,且对重金属等具有良好的吸附性,无需修饰或预处理,即可作为重金属生物吸附剂,具有大规模生产的潜力。The present invention provides a method for recovering rare earth elements from red mud by using acidophilic thermophilic red algae. The red mud extract is mixed with acidophilic thermophilic red algae seed liquid, and the mixture is recovered and cultured to realize the recovery of rare earth elements in the red mud. The acidophilic thermophilic red algae seed liquid is an algae liquid rich in unicellular red algae G. sulphuraria, the algae species number is G. sulphuraria UTEX 2919, which is purchased from the algae seed bank of the University of Texas (UTEX), and the optical picture is shown in FIG1. The acidophilic thermophilic red algae can survive in adverse ecological environments such as acidic hot sulfur springs, sulfur pores, open-pit mines and endogenous rocks, and can withstand high temperature (up to 63° C.), strong acid (pH 0-4.0), high osmotic pressure (9% salinity) and high concentration of heavy metals (such as chromium, nickel) and other extreme environments, and has good adsorption to heavy metals, etc., and can be used as a heavy metal biosorbent without modification or pretreatment, and has the potential for large-scale production.

在本发明实施例中,利用嗜酸嗜热红藻从赤泥中回收稀土元素的方法具体包括以下步骤:In an embodiment of the present invention, the method for recovering rare earth elements from red mud using acidophilic thermophilic red algae specifically comprises the following steps:

(1)将赤泥与提取液混合,振荡、离心,取上清液,得到赤泥浸提液;(1) mixing red mud and extract, shaking, centrifuging, and taking the supernatant to obtain red mud extract;

(2)将所述赤泥浸提液、嗜酸嗜热红藻种液和碳源混合,得到待回收处理液;(2) mixing the red mud extract, the acidophilic and thermophilic red algae seed solution and the carbon source to obtain a treated solution to be recovered;

(3)将所述待回收处理液进行回收培养,离心沉降分离吸附有稀土元素的嗜酸嗜热红藻,用去离子水冲洗2-3遍,加入解吸附剂,振荡,利用嗜酸嗜热红藻(G.sulphuraria)对待回收处理液进行净化,即可实现赤泥中稀土元素的回收。(3) The treated liquid to be recovered is cultured and centrifuged to separate the acidophilic thermophilic red algae adsorbing the rare earth elements, and the treated liquid is rinsed with deionized water for 2-3 times, a desorbent is added, and the treated liquid is shaken. The acidophilic thermophilic red algae (G. sulphuraria) is used to purify the treated liquid to be recovered, thereby realizing the recovery of rare earth elements in red mud.

作为优选,所述解吸附剂为浓度0.1mol/L的HNO3Preferably, the desorbent is HNO 3 with a concentration of 0.1 mol/L.

作为优选,足本发明实施例中嗜酸嗜热红藻种液制备方法为:在室温下,将单细胞红藻G.sulphuraria接种于盛有BG-11培养基(培养基成分见表1)的锥形瓶中进行预培养,初始接种浓度为0.44g/L,培养时间为7天,光照强度为2500lx,光暗比12h∶12h,得到嗜酸嗜热红藻种液。Preferably, the method for preparing the acidophilic thermophilic red algae seed solution in the embodiment of the present invention is as follows: at room temperature, the unicellular red algae G. sulphuraria is inoculated into a conical flask containing BG-11 culture medium (the culture medium components are shown in Table 1) for pre-culture, the initial inoculation concentration is 0.44 g/L, the culture time is 7 days, the light intensity is 2500 lx, the light-dark ratio is 12h:12h, and the acidophilic thermophilic red algae seed solution is obtained.

作为优选,所述提取液为10%的硝酸溶液,赤泥与提取液的固液比为1kg∶50L。使用硝酸浸提赤泥的目的是:使赤泥中的钪、钛等稀土元素以离子形式进入酸浸液,便于嗜酸嗜热红藻通过细胞代谢富集稀土元素,以实现稀土元素的回收。Preferably, the extract is a 10% nitric acid solution, and the solid-liquid ratio of red mud to the extract is 1 kg: 50 L. The purpose of using nitric acid to extract red mud is to allow rare earth elements such as scandium and titanium in the red mud to enter the acid leaching solution in the form of ions, so that the acidophilic thermophilic red algae can enrich the rare earth elements through cell metabolism to achieve the recovery of rare earth elements.

作为优选,步骤(1)中,在室温下振荡10h后,在2000g条件下离心10min。经过振荡、离心处理,赤泥中的大部分稀土元素在酸浸条件下可以以离子形式转入液相。Preferably, in step (1), after shaking at room temperature for 10 hours, centrifugation is performed at 2000 g for 10 minutes. After shaking and centrifugation, most of the rare earth elements in the red mud can be transferred into the liquid phase in the form of ions under acid leaching conditions.

作为优选,所述待回收处理液中,赤泥浸提液的体积为10%。Preferably, the volume of red mud extract in the treated liquid to be recovered is 10%.

作为优选,所述碳源包括甘油或葡萄糖中的一种或两种,碳源在待回收处理液中的添加量为20-40g/L。添加碳源的作用为使微藻利用外加碳源进行异养或兼养生长,能够促进微藻的生长代谢,提升微藻对稀土元素的富集速率。Preferably, the carbon source includes one or both of glycerol or glucose, and the amount of the carbon source added to the treated liquid to be recycled is 20-40 g/L. The role of adding the carbon source is to enable the microalgae to grow heterotrophically or mixotrophically using the added carbon source, which can promote the growth and metabolism of the microalgae and increase the enrichment rate of the microalgae for rare earth elements.

作为优选,所述待回收处理液中,嗜酸嗜热红藻初始细胞密度为1.8×106cells/mL。控制嗜酸嗜热红藻的初始细胞密度,目的在于控制嗜酸嗜热红藻的生物量浓度,浓度过大会导致嗜酸嗜热红藻对光照、养分等物质的竞争,抑制微藻的生长,过低会导致嗜酸嗜热红藻对稀土元素的富集效率下降。Preferably, in the treated liquid to be recycled, the initial cell density of the acidophilic thermophilic red algae is 1.8×10 6 cells/mL. The initial cell density of the acidophilic thermophilic red algae is controlled to control the biomass concentration of the acidophilic thermophilic red algae. Too high a concentration will cause the acidophilic thermophilic red algae to compete with light, nutrients and other substances, inhibiting the growth of microalgae. Too low a concentration will cause the acidophilic thermophilic red algae to reduce the enrichment efficiency of rare earth elements.

作为优选,所述回收培养的温度为40℃,湿度为50~70%,时间为5-10d,pH为2.5~4,优选,pH为3.5。回收培养过程的关键点在于调整适宜的培养条件实现嗜酸嗜热红藻对稀土元素的最大富集率。Preferably, the temperature of the recovery culture is 40°C, the humidity is 50-70%, the time is 5-10 days, the pH is 2.5-4, preferably, the pH is 3.5. The key point of the recovery culture process is to adjust the appropriate culture conditions to achieve the maximum enrichment rate of rare earth elements by acidophilic thermophilic red algae.

作为优选,所述回收培养在光照(全光谱LED灯)下进行,光照强度为8000~12000Lx,光暗周期比为16h:8h。光照情况下,嗜酸嗜热红藻通过细胞代谢富集稀土元素。Preferably, the recovery culture is carried out under illumination (full spectrum LED light), the illumination intensity is 8000-12000Lx, and the light-dark cycle ratio is 16h:8h. Under illumination, the acidophilic and thermophilic red algae enrich rare earth elements through cell metabolism.

本发明实施例所用各原料均为通过市售购买得到。All raw materials used in the embodiments of the present invention are purchased from commercial sources.

本发明实施例中室温是指25±2℃。The room temperature in the embodiments of the present invention refers to 25±2°C.

本发明实施例中赤泥采集自某城市氧化铝生产企业的赤泥堆场。In the embodiments of the present invention, the red mud is collected from the red mud dump of an alumina production enterprise in a certain city.

G.sulphuraria对赤泥浸提液的耐受性Tolerance of G. sulphuraria to red mud extract

将赤泥与提取液(体积分数为10%的硝酸溶液)以固液比为1:50(kg·L-1)进行混合,在室温下振荡10h后,在2000g条件下离心10min,取上清液,得到赤泥浸提液;将嗜酸嗜热红藻种液(G.sulphuraria)接种于300mL含有赤泥浸提液(RM)的2MA培养基(培养基组成见表2,赤泥浸提液在2MA培养基中的含量为30mL)中,为RM组,测定初始OD700为0.1,培养条件为40℃,10000Lx光照下通气培养。接种后,每天检测红藻培养物的OD700值,制作成生长曲线,以用2MA培养基培养直接培养嗜酸嗜热红藻种液(G.sulphuraria)为对照组,观察G.sulphuraria对赤泥浸提液的耐受性,生长曲线结果见图2。The red mud and the extract (10% nitric acid solution by volume) were mixed at a solid-liquid ratio of 1:50 (kg·L -1 ), and after shaking at room temperature for 10 hours, the mixture was centrifuged at 2000g for 10 minutes, and the supernatant was taken to obtain the red mud extract; the acidophilic thermophilic red algae seed solution (G. sulphuraria) was inoculated into 300 mL of 2MA medium containing red mud extract (RM) (the composition of the medium is shown in Table 2, and the content of the red mud extract in the 2MA medium is 30 mL), which is the RM group, and the initial OD 700 was determined to be 0.1, and the culture conditions were 40°C and aerated culture under 10000Lx light. After inoculation, the OD 700 value of the red algae culture was detected every day, and a growth curve was prepared. The acidophilic thermophilic red algae seed solution (G. sulphuraria) directly cultured in 2MA medium was used as the control group to observe the tolerance of G. sulphuraria to the red mud extract, and the growth curve results are shown in Figure 2.

表2 2MA培养基组成Table 2 Composition of 2MA medium

由图2可以看出,G.sulphuraria在2MA培养基中培养的生长曲线(对照组)与添加有赤泥浸提液(RM)的2MA培养基中培养的生长曲线(RM组)相差不大,可见G.sulphuraria对赤泥浸提液(RM)的耐受力比较高,因此能够将G.sulphuraria应用于赤泥回收处理中,以下通过实施例对本发明的技术方案做进一步说明。具体实施例如下:As can be seen from Figure 2, the growth curve of G. sulphuraria cultured in 2MA medium (control group) is not much different from the growth curve of G. sulphuraria cultured in 2MA medium added with red mud extract (RM) (RM group), which shows that G. sulphuraria has a relatively high tolerance to red mud extract (RM), so G. sulphuraria can be applied to red mud recovery and treatment. The technical solution of the present invention is further described by examples below. Specific examples are as follows:

实施例1Example 1

(1)将赤泥与提取液(体积分数为10%的硝酸溶液)以固液比为1:50(kg·L-1)混合,在室温下振荡10h后,在2000g条件下离心10min,取上清液,得到赤泥浸提液;(1) Red mud and an extract (10% nitric acid solution by volume) were mixed at a solid-liquid ratio of 1:50 (kg·L -1 ), shaken at room temperature for 10 h, and then centrifuged at 2000 g for 10 min to obtain a supernatant to obtain a red mud extract;

(2)将赤泥浸提液、嗜酸嗜热红藻种液和碳源(葡萄糖,在待回收处理液中的添加量为40g/L)混合,得到待回收处理液,待回收处理液中赤泥浸提液的体积为10%,嗜酸嗜热红藻初始细胞密度为1.8×106cells/mL;(2) mixing the red mud extract, the acidophilic thermophilic red algae seed solution and the carbon source (glucose, added in the to-be-recovered treatment liquid in an amount of 40 g/L) to obtain the to-be-recovered treatment liquid, wherein the volume of the red mud extract in the to-be-recovered treatment liquid is 10%, and the initial cell density of the acidophilic thermophilic red algae is 1.8×10 6 cells/mL;

(3)将待回收处理液进行回收培养,温度为40℃,湿度为70%,时间为10d,pH为2.5,在全光谱LED灯下进行,光照强度为10000Lx,光暗周期比为16h:8h,通过离心沉降法回收富集了稀土元素的嗜酸嗜热红藻,用去离子水冲洗2-3遍,用0.1mol/L的HNO3作为解吸附剂与嗜酸嗜热红藻混合并充分振荡,解吸藻细胞富集的稀土离子,利用嗜酸嗜热红藻(G.sulphuraria)对待回收处理液进行净化,即可实现赤泥中稀土元素的回收。(3) The treated liquid to be recovered is cultured at a temperature of 40°C, a humidity of 70%, a time of 10 days, a pH of 2.5, under a full-spectrum LED lamp, a light intensity of 10,000 Lx, a light-dark cycle ratio of 16 h:8 h, and the acidophilic thermophilic red algae enriched with rare earth elements are recovered by centrifugal sedimentation, rinsed with deionized water 2-3 times, and mixed with the acidophilic thermophilic red algae using 0.1 mol/L HNO3 as a desorbent and fully shaken to desorb the rare earth ions enriched in the algae cells. The treated liquid to be recovered is purified by the acidophilic thermophilic red algae (G. sulphuraria), thereby realizing the recovery of rare earth elements in red mud.

本实施例通过嗜酸嗜热红藻(G.sulphuraria)对待回收处理液中的赤泥中稀土元素进行富集,并进一步分离,实现赤泥中稀土元素的回收。In this embodiment, the rare earth elements in the red mud in the treatment liquid to be recovered are enriched by acidophilic thermophilic red algae (G. sulphuraria), and further separated to achieve the recovery of rare earth elements in the red mud.

实施例2Example 2

同实施例1,区别仅在于,回收培养的pH为3。Same as Example 1, except that the pH of the recovery culture is 3.

实施例3Example 3

同实施例1,区别仅在于,回收培养的pH为3.5。Same as Example 1, except that the pH of the recovery culture is 3.5.

实施例4Example 4

同实施例1,区别仅在于,回收培养的pH为4。Same as Example 1, except that the pH of the recovery culture is 4.

实施例5Example 5

(1)将赤泥与提取液(体积分数为10%的硝酸溶液,固液比为1:50(kg·L-1))混合,在室温下振荡10h后,在2000g条件下离心10min,取上清液,得到赤泥浸提液;(1) Red mud was mixed with an extract (10% nitric acid solution by volume, solid-liquid ratio of 1:50 (kg·L -1 )), shaken at room temperature for 10 h, centrifuged at 2000 g for 10 min, and the supernatant was collected to obtain a red mud extract;

(2)将赤泥浸提液、嗜酸嗜热红藻种液和碳源(葡萄糖,在待回收处理液的添加量为40g/L)混合,得到待回收处理液,待回收处理液中赤泥浸提液的体积为10%,嗜酸嗜热红藻初始细胞密度为1.8×106cells/mL;(2) mixing the red mud extract, the acidophilic thermophilic red algae seed solution and the carbon source (glucose, added in the recovery treatment liquid at an amount of 40 g/L) to obtain the recovery treatment liquid, wherein the volume of the red mud extract in the recovery treatment liquid is 10%, and the initial cell density of the acidophilic thermophilic red algae is 1.8×10 6 cells/mL;

(3)将待回收处理液进行回收培养,温度为40℃,湿度为50%,时间为10d,pH为3.5,在全光谱LED灯下进行,光照强度为10000Lx,光暗周期比为16h:8h,通过离心沉降法回收富集了稀土元素的嗜酸嗜热红藻,用去离子水冲洗2-3遍,用0.1mol/L的HNO3作为解吸附剂与嗜酸嗜热红藻混合并充分振荡,解吸藻细胞富集的稀土离子,利用嗜酸嗜热红藻(G.sulphuraria)对待回收处理液进行净化,即可实现赤泥中稀土元素的回收。(3) The treated liquid to be recovered is cultured at a temperature of 40°C, a humidity of 50%, a time of 10 days, a pH of 3.5, under a full-spectrum LED lamp, a light intensity of 10,000 Lx, a light-dark cycle ratio of 16 h:8 h, and the acidophilic thermophilic red algae enriched with rare earth elements is recovered by centrifugal sedimentation, rinsed with deionized water 2-3 times, and mixed with the acidophilic thermophilic red algae using 0.1 mol/L HNO3 as a desorbent and fully shaken to desorb the rare earth ions enriched in the algae cells. The treated liquid to be recovered is purified by the acidophilic thermophilic red algae (G. sulphuraria), thereby realizing the recovery of rare earth elements in red mud.

实施例6Example 6

(1)将赤泥与提取液(体积分数为10%的硝酸溶液,固液比为1:50(kg/L))混合,在室温下振荡10h后,在2000g条件下离心10min,取上清液,得到赤泥浸提液;(1) red mud and an extract (10% nitric acid solution by volume, solid-liquid ratio of 1:50 (kg/L)) were mixed, shaken at room temperature for 10 h, centrifuged at 2000 g for 10 min, and the supernatant was collected to obtain a red mud extract;

(2)将赤泥浸提液、嗜酸嗜热红藻种液和碳源(葡萄糖,在待回收处理液中的添加量为40g/L)混合,得到待回收处理液,待回收处理液中赤泥浸提液的体积为10%,嗜酸嗜热红藻初始细胞密度为1.8×106cells/mL;(2) mixing the red mud extract, the acidophilic thermophilic red algae seed solution and the carbon source (glucose, added in the to-be-recovered treatment liquid in an amount of 40 g/L) to obtain the to-be-recovered treatment liquid, wherein the volume of the red mud extract in the to-be-recovered treatment liquid is 10%, and the initial cell density of the acidophilic thermophilic red algae is 1.8×10 6 cells/mL;

(3)将待回收处理液进行回收培养,温度为40℃,湿度为60%,时间为10d,pH为3.5,在全光谱LED灯下进行,光照强度为12000Lx,光暗周期比为16h:8h,,通过离心沉降法回收富集了稀土元素的嗜酸嗜热红藻,用去离子水冲洗2-3遍,用0.1mol/L的HNO3作为解吸附剂与嗜酸嗜热红藻混合并充分振荡,解吸藻细胞富集的稀土离子,利用嗜酸嗜热红藻(G.sulphuraria)对待回收处理液进行净化,即可实现赤泥中稀土元素的回收。(3) The treated liquid to be recovered is cultured at a temperature of 40°C, a humidity of 60%, a time of 10 days, a pH of 3.5, under a full-spectrum LED lamp, a light intensity of 12000Lx, a light-dark cycle ratio of 16h:8h, and the acidophilic thermophilic red algae enriched with rare earth elements are recovered by centrifugal sedimentation, rinsed with deionized water 2-3 times, mixed with 0.1mol/L HNO3 as a desorbent and fully shaken to desorb the rare earth ions enriched in the algae cells, and the acidophilic thermophilic red algae (G. sulphuraria) are used to purify the treated liquid to be recovered, thereby realizing the recovery of rare earth elements in red mud.

对比例1Comparative Example 1

同实施例5,区别仅在于,不加入赤泥浸提液:将嗜酸嗜热红藻种液和碳源(葡萄糖,在待回收处理液的添加量为40g/L)混合,得到待回收处理液,嗜酸嗜热红藻初始细胞密度为1.8×106cells/mL;将待回收处理液进行回收培养,温度为40℃,湿度为50%,时间为10d,pH为3.5,在全光谱LED灯下进行,光照强度为10000Lx,光暗周期比为16h:8h。The same as Example 5, except that no red mud extract is added: the acidophilic thermophilic red algae seed solution and the carbon source (glucose, added in an amount of 40 g/L in the treated liquid to be recovered) are mixed to obtain a treated liquid to be recovered, and the initial cell density of the acidophilic thermophilic red algae is 1.8×10 6 cells/mL; the treated liquid to be recovered is recovered and cultured at a temperature of 40° C., a humidity of 50%, a time of 10 d, a pH of 3.5, under a full-spectrum LED lamp, a light intensity of 10000 Lx, and a light-dark cycle ratio of 16h:8h.

对比例2Comparative Example 2

同实施例5,区别仅在于,葡萄糖在待回收处理液的添加量为15g/L。The same as Example 5, except that the amount of glucose added to the treated liquid to be recovered is 15 g/L.

对比例3Comparative Example 3

同实施例5,区别仅在于,步骤(3)回收培养的时间为4d,回收培养的温度为40℃,湿度为50%,时间为10d,pH为3.5,在全光谱LED灯下进行,光照强度为10000Lx,光暗周期比为16h:8h。The same as Example 5, except that the recovery culture time in step (3) is 4 days, the recovery culture temperature is 40°C, the humidity is 50%, the time is 10 days, the pH is 3.5, and it is carried out under full-spectrum LED light, the light intensity is 10000Lx, and the light-dark cycle ratio is 16h:8h.

对比例4Comparative Example 4

同实施例6,区别仅在于,光照强度为15000Lx,回收培养的温度为40℃,湿度为60%,时间为10d,pH为3.5,在全光谱LED灯下进行,光暗周期比为16h:8h。Same as Example 6, except that the light intensity is 15000 Lx, the temperature of the recovery culture is 40°C, the humidity is 60%, the time is 10 days, the pH is 3.5, it is carried out under full-spectrum LED light, and the light-dark cycle ratio is 16h:8h.

性能测试Performance Testing

G.sulphuraria在生长进入稳定期后,分别在2000g条件下离心收集实施例以及对比例中的藻细胞,并用ICP-MS检测红藻中吸收富集的稀土元素。After the growth of G. sulphuraria entered the stable phase, the algae cells in the embodiment and the comparative example were collected by centrifugation at 2000 g, and the rare earth elements absorbed and enriched in the red algae were detected by ICP-MS.

实施例1-4的实验结果表明培养pH在2.5-4.0之间时红藻对铈(Ce)、镧(La)、钇(Y)、钕(Nd)、镨(Pr)、钐(Sm)、钆(Gd)均有富集效果,另外,实施例1-4不同pH下细胞中总稀土元素含量测定结果见图3,由图3可以看出,pH值为3.5时,富集效率最高;pH值为2.5时,富集效率较低。因此红藻从赤泥中回收稀土元素的最佳培养pH值为3.5左右。The experimental results of Examples 1-4 show that when the culture pH is between 2.5-4.0, red algae have an enrichment effect on cerium (Ce), lanthanum (La), yttrium (Y), neodymium (Nd), praseodymium (Pr), samarium (Sm), and gadolinium (Gd). In addition, the results of the determination of the total rare earth element content in cells at different pH values in Examples 1-4 are shown in Figure 3. As can be seen from Figure 3, when the pH value is 3.5, the enrichment efficiency is the highest; when the pH value is 2.5, the enrichment efficiency is relatively low. Therefore, the optimal culture pH value for red algae to recover rare earth elements from red mud is about 3.5.

测得实施例5与对比例1(control/对照)吸收富集的单一稀土元素的浓度结果见图4和表3。The concentration of a single rare earth element absorbed and enriched in Example 5 and Comparative Example 1 (control) is measured and shown in FIG4 and Table 3.

表3实施例5与对比例1对各稀土元素的富集效果(μg/g干重)Table 3 Enrichment effect of Example 5 and Comparative Example 1 on each rare earth element (μg/g dry weight)

YY LaLa CeCe PrPr NdNd SmSm EuEu GdG TbTb DyDy ErEr TmTm YbYb 对比例1Comparative Example 1 0.210.21 0.220.22 0.350.35 0.340.34 0.350.35 0.300.30 0.250.25 0.410.41 0.230.23 0.330.33 0.420.42 0.530.53 1.121.12 实施例5Example 5 10.3110.31 10.7410.74 26.4226.42 4.824.82 16.1416.14 3.423.42 1.241.24 3.113.11 0.540.54 2.832.83 1.511.51 0.330.33 2.322.32

结合图4和表3可以看出,G.sulphuraria对铈(Ce)、镧(La)、钇(Y)、钕(Nd)、镨(Pr)、钐(Sm)、钆(Gd)均有吸收富集效果,且对Ce、Nd、La和Y吸收效果较好。From Figure 4 and Table 3, it can be seen that G. sulphuraria has an absorption and enrichment effect on cerium (Ce), lanthanum (La), yttrium (Y), neodymium (Nd), praseodymium (Pr), samarium (Sm), and gadolinium (Gd), and has a better absorption effect on Ce, Nd, La, and Y.

测得实施例5与对比例1(control/对照)吸收富集的总稀土元素浓度结果见图5,由图5可以看出,实施例5中G.sulphuraria生物量中累积的总稀土元素浓度,相对于对比例1而言,藻细胞内吸收的稀土浓度达到121.5μg/g干重,证明该种红藻能够在酸性的赤泥浸提液中生存,且对赤泥浸提液中的稀土金属有着良好富集效果。The results of the total rare earth element concentration absorbed and enriched in Example 5 and Comparative Example 1 (control) are shown in Figure 5. As can be seen from Figure 5, the total rare earth element concentration accumulated in the biomass of G. sulphuraria in Example 5, relative to that in Comparative Example 1, the rare earth concentration absorbed in the algae cells reached 121.5 μg/g dry weight, proving that this type of red algae can survive in the acidic red mud extract and has a good enrichment effect on the rare earth metals in the red mud extract.

实施例3、实施例5、实施例6以及对比例2-4方法中G.sulphuraria生物量中累积的总稀土元素浓度结果见图6。测得实施例5中G.sulphuraria生物量中累积的总稀土元素浓度略低于实施例3,实施例3和实施例5的藻细胞内吸收的稀土浓度分别达到125.1μg/g和121.5μg/g干重,证明该种红藻在培养条件为湿度为50~70%能够实现较高的富集效率;测得实施例5中G.sulphuraria生物量中累积的总稀土元素浓度远高于对比例2、3,说明该种红藻在碳源(葡萄糖)投加量低于20g/L或培养时间少于5d的培养条件下富集稀土元素的效率很低,证明该种红藻适宜的培养条件为碳源投加量为20-40g/L,时间为5-10d;实施例6中G.sulphuraria生物量中累积的总稀土元素浓度远高于对比例4,证明光照强度高于12000lx时,嗜酸嗜热红藻的富集效率下降,该种红藻的适宜培养条件为在全光谱LED灯下进行,光照强度为8000~12000Lx,光暗周期比为16h:8h。The results of the total rare earth element concentration accumulated in the biomass of G. sulphuraria in the methods of Examples 3, 5, 6 and Comparative Examples 2-4 are shown in Figure 6. The total rare earth element concentration accumulated in the biomass of G. sulphuraria in Example 5 was slightly lower than that in Example 3. The rare earth concentrations absorbed in the algae cells of Examples 3 and 5 reached 125.1 μg/g and 121.5 μg/g dry weight, respectively, proving that the red algae can achieve a higher enrichment efficiency under the culture condition of 50-70% humidity; the total rare earth element concentration accumulated in the biomass of G. sulphuraria in Example 5 was much higher than that in Comparative Examples 2 and 3, indicating that the red algae can achieve a higher enrichment efficiency when the carbon source (glucose) addition amount is less than 20 g/L. Or the efficiency of enriching rare earth elements under the culture condition of less than 5 days is very low, which proves that the suitable culture condition of this red algae is a carbon source addition amount of 20-40g/L and a culture time of 5-10d; the total rare earth element concentration accumulated in the biomass of G.sulphuraria in Example 6 is much higher than that in Comparative Example 4, which proves that when the light intensity is higher than 12000lx, the enrichment efficiency of acidophilic thermophilic red algae decreases, and the suitable culture condition of this red algae is under full-spectrum LED lamp, the light intensity is 8000-12000Lx, and the light-dark cycle ratio is 16h:8h.

以上,仅为本申请较佳的具体实施方式,但本申请的保护范围并不局限于此,任何熟悉本技术领域的技术人员在本申请揭露的技术范围内,可轻易想到的变化或替换,都应涵盖在本申请的保护范围之内。因此,本申请的保护范围应该以权利要求的保护范围为准。The above are only preferred specific implementations of the present application, but the protection scope of the present application is not limited thereto. Any changes or substitutions that can be easily thought of by a person skilled in the art within the technical scope disclosed in the present application should be included in the protection scope of the present application. Therefore, the protection scope of the present application should be based on the protection scope of the claims.

Claims (5)

1.一种利用嗜酸嗜热红藻从赤泥中回收稀土元素的方法,其特征在于,将赤泥浸提液与嗜酸嗜热红藻种液混合,利用嗜酸嗜热红藻进行净化,实现赤泥中稀土元素的回收,所述嗜酸嗜热红藻种液为富含单细胞红藻G.sulphuraria的藻液;具体包括以下步骤:1. A method for recovering rare earth elements from red mud using acidophilic thermophilic red algae, characterized in that red mud extract is mixed with acidophilic thermophilic red algae seed solution, and the acidophilic thermophilic red algae is used for purification to achieve recovery of rare earth elements in red mud, wherein the acidophilic thermophilic red algae seed solution is an algae solution rich in unicellular red algae G. sulphuraria; specifically comprising the following steps: 将赤泥与提取液混合,振荡、离心,取上清液,得到赤泥浸提液,将所述赤泥浸提液、嗜酸嗜热红藻种液和碳源混合,得到待回收处理液,将所述待回收处理液进行回收培养,离心沉降分离吸附有稀土元素的嗜酸嗜热红藻,洗涤,加入解吸附剂,振荡,实现赤泥中稀土元素的富集和回收;The red mud is mixed with the extract, shaken, centrifuged, and the supernatant is taken to obtain a red mud extract, the red mud extract, the acidophilic thermophilic red algae seed solution and the carbon source are mixed to obtain a treatment solution to be recovered, the treatment solution to be recovered is recovered and cultured, the acidophilic thermophilic red algae adsorbed with rare earth elements are separated by centrifugal sedimentation, washed, a desorbent is added, and shaken to achieve the enrichment and recovery of rare earth elements in the red mud; 所述提取液为体积分数为10%的硝酸溶液,赤泥与提取液的固液比为1kg∶50L;The extract is a nitric acid solution with a volume fraction of 10%, and the solid-liquid ratio of red mud to the extract is 1kg:50L; 所述碳源包括甘油或葡萄糖中的一种或两种,碳源在待回收处理液中的添加量为20-40g/L;The carbon source includes one or both of glycerol and glucose, and the amount of the carbon source added to the treated liquid to be recovered is 20-40 g/L; 所述回收培养的pH为3~4;The pH of the recovery culture is 3 to 4; 所述回收培养的温度为40℃,湿度为50~70%,时间为5-10d;The recovery culture temperature is 40°C, the humidity is 50-70%, and the time is 5-10 days; 所述回收培养在光照下进行,光照强度为8000~12000Lx,光暗周期比为16h:8h。The recovery culture is carried out under light, the light intensity is 8000-12000Lx, and the light-dark cycle ratio is 16h:8h. 2.根据权利要求1所述的利用嗜酸嗜热红藻从赤泥中回收稀土元素的方法,其特征在于,在室温下振荡10h后,在2000g条件下离心10min。2. The method for recovering rare earth elements from red mud using acidophilic and thermophilic red algae according to claim 1, characterized in that after shaking at room temperature for 10 hours, centrifugation is performed at 2000g for 10 minutes. 3.根据权利要求1所述的利用嗜酸嗜热红藻从赤泥中回收稀土元素的方法,其特征在于,所述待回收处理液中,赤泥浸提液的体积为10%。3. The method for recovering rare earth elements from red mud using acidophilic and thermophilic red algae according to claim 1, characterized in that the volume of the red mud extract in the treated liquid to be recovered is 10%. 4.根据权利要求1所述的利用嗜酸嗜热红藻从赤泥中回收稀土元素的方法,其特征在于,所述待回收处理液中,嗜酸嗜热红藻初始细胞密度为1.8×106cells/mL。4. The method for recovering rare earth elements from red mud using acidophilic thermophilic red algae according to claim 1, characterized in that the initial cell density of the acidophilic thermophilic red algae in the treated liquid to be recovered is 1.8×10 6 cells/mL. 5.权利要求1~4任一项所述方法在赤泥回收处理中的应用。5. Application of the method according to any one of claims 1 to 4 in red mud recovery and treatment.
CN202311022382.3A 2023-08-15 2023-08-15 A method and application of recovering rare earth elements from red mud using acidophilic thermophilic red algae Active CN117025985B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202311022382.3A CN117025985B (en) 2023-08-15 2023-08-15 A method and application of recovering rare earth elements from red mud using acidophilic thermophilic red algae

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202311022382.3A CN117025985B (en) 2023-08-15 2023-08-15 A method and application of recovering rare earth elements from red mud using acidophilic thermophilic red algae

Publications (2)

Publication Number Publication Date
CN117025985A CN117025985A (en) 2023-11-10
CN117025985B true CN117025985B (en) 2024-04-05

Family

ID=88601891

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202311022382.3A Active CN117025985B (en) 2023-08-15 2023-08-15 A method and application of recovering rare earth elements from red mud using acidophilic thermophilic red algae

Country Status (1)

Country Link
CN (1) CN117025985B (en)

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CA2868962A1 (en) * 2012-03-30 2013-10-03 Nippon Light Metal Company, Ltd. Method of recovering rare-earth elements
CN109161684A (en) * 2018-11-12 2019-01-08 江西理工大学 A method of utilizing spirulina recovering rare earth
CN110170295A (en) * 2019-06-13 2019-08-27 昆明理工大学 A kind of dephosphorization adsorbent and preparation method thereof
WO2022049239A1 (en) * 2020-09-03 2022-03-10 Darina Styriakova Ecological release of elements and degradation of organics using heterotrophic microorganisms out of multiple carrier materials
CN115505740A (en) * 2022-09-29 2022-12-23 南京江岛环境科技研究院有限公司 A resource recovery method for treating red mud with nitrate wastewater

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CA2868962A1 (en) * 2012-03-30 2013-10-03 Nippon Light Metal Company, Ltd. Method of recovering rare-earth elements
CN109161684A (en) * 2018-11-12 2019-01-08 江西理工大学 A method of utilizing spirulina recovering rare earth
CN110170295A (en) * 2019-06-13 2019-08-27 昆明理工大学 A kind of dephosphorization adsorbent and preparation method thereof
WO2022049239A1 (en) * 2020-09-03 2022-03-10 Darina Styriakova Ecological release of elements and degradation of organics using heterotrophic microorganisms out of multiple carrier materials
CN115505740A (en) * 2022-09-29 2022-12-23 南京江岛环境科技研究院有限公司 A resource recovery method for treating red mud with nitrate wastewater

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
Biotechnological trends and market impact on the recovery of rare earth elements from bauxite residue (red mud) - A review;Sandeep Panda et al;Resources,Conservation & Recycling;1-15 *
Recovery of rare earth elements from the sulfothermophilic red alga Galdieria sulphuraria using aqueous acid;Minoda et al;Appl Microbiol Biotechnol;1-7 *

Also Published As

Publication number Publication date
CN117025985A (en) 2023-11-10

Similar Documents

Publication Publication Date Title
CN111389363B (en) Magnetic biochar adsorbing material based on sulfate-reduced sludge and preparation method and application thereof
CN104630295B (en) A kind of method for handling city secondary waste water using immobilized microalgae and producing grease
CN103723894B (en) A kind of New treatment method of threonine mother liquid
CN102730784A (en) Method for removing nitrogen and phosphorus by modifying sintered red mud
CN104591459A (en) Acid and alkali resource recovery process technology from sodium saponification waste water
CN107434305A (en) A kind of water purification agent of rich defect carbon carrier fixation of microbe and preparation method thereof
CN113083219A (en) Method for preparing denitrification and dephosphorization adsorbent from yellow phosphorus slag and application
CN111530410A (en) A method for preparing phosphorus removal adsorbent based on natural zeolite synthetic molecular sieve waste
CN115814750B (en) Method for preparing porous calcium silicate adsorbent from phosphogypsum
CN111661943B (en) Comprehensive biogas slurry utilization method
CN102350313B (en) Preparation method and application of copper and ferrous magnetic metal oxide modified fly ash phosphorus adsorbent
CN115403161A (en) A kind of microalgae self-flocculation particle, its preparation method and application
CN117025985B (en) A method and application of recovering rare earth elements from red mud using acidophilic thermophilic red algae
CN108383220A (en) A kind of method of sewage microalgae and synchronous nitrogen and phosphorus trapping recycling
CN111875052B (en) Montmorillonite-pyrite composite biological carrier material and preparation method and application method thereof
CN118479434B (en) A method for efficiently recovering phosphorus from microalgae to prepare blue iron ore
CN114807639B (en) Light-driven microbial uranium ore leaching method
CN116333886B (en) Single-cell green algae capable of producing oil and application thereof
CN111729646B (en) A kind of EGCG-iron particulate green material for removing phosphorus in water and its preparation method and application
CN105753063A (en) Method for separating ferric oxide in coal-powder boiler fly ash
CN116949288A (en) Method for absorbing and recovering rare earth ions in culturing process of bacillus subtilis
CN105776344A (en) Method for separating Fe2O3 in pulverized coal ash of circulating fluidized bed
CN117105422A (en) Method for treating cassava starch wastewater by utilizing microalgae fungus symbiotic system
CN119186485A (en) Iron-magnesium modified sepiolite composite material, preparation method thereof and application of iron-magnesium modified sepiolite composite material as dephosphorization and algae inhibition functional material
CN117482928A (en) A rare earth metal ion adsorption material and its preparation method

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant