CN104787902A - Method for adsorbing heavy metal in wastewater by using mold spore - Google Patents
Method for adsorbing heavy metal in wastewater by using mold spore Download PDFInfo
- Publication number
- CN104787902A CN104787902A CN201510226403.2A CN201510226403A CN104787902A CN 104787902 A CN104787902 A CN 104787902A CN 201510226403 A CN201510226403 A CN 201510226403A CN 104787902 A CN104787902 A CN 104787902A
- Authority
- CN
- China
- Prior art keywords
- mold
- heavy metals
- mold spores
- spores
- wastewater
- 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.)
- Pending
Links
Landscapes
- Micro-Organisms Or Cultivation Processes Thereof (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
Abstract
一种利用霉菌孢子吸附废水中重金属的方法,它涉及一种利用霉菌孢子吸附废水中重金属的方法,本发明是要解决现有霉菌菌丝球粉末吸附剂吸附效果差以及成本高的问题,本发明方法为:一、将霉菌孢子接种于固体培养基上,在30℃的条件下培养,然后收集霉菌气生菌丝上自然脱落的霉菌孢子;二、将步骤一收集的霉菌孢子投加到含重金属的废水中,即完成;本发明的优点是孢子的收集可以简化吸附剂制备步骤,节约成本的同时提高重金属吸附量。本发明应用于吸附剂领域。A method for using mold spores to adsorb heavy metals in wastewater, which relates to a method for using mold spores to adsorb heavy metals in wastewater. The present invention aims to solve the problems of poor adsorption effect and high cost of existing mold mycelium ball powder adsorbents. The present invention The inventive method is as follows: 1. Inoculate the mold spores on the solid medium, cultivate them at 30°C, and then collect the mold spores that naturally fall off from the aerial hyphae of the mold; 2. Add the mold spores collected in step 1 to the In wastewater containing heavy metals, it is completed; the advantage of the invention is that the collection of spores can simplify the preparation steps of the adsorbent, save costs and increase the adsorption capacity of heavy metals at the same time. The invention is applied in the field of adsorbents.
Description
技术领域technical field
本发明涉及一种吸附废水中重金属的方法。The invention relates to a method for adsorbing heavy metals in waste water.
背景技术Background technique
传统的重金属去除技术:对于重金属的去除传统的方法有化学沉降、氧化还原、离子交换、电化学处理、过滤、反渗透、溶剂萃取及蒸发回收等。各种物理、化学的方法也只是重金属离子的转移、浓缩、或存在形式改变,重金属不会消失,总量不会减少,这是重金属废水有别于其它废水之处。早些年,离子交换法应用较广泛,但由于树脂成本较高,对原有水质有一定的限制,如废水中有机物和氧化物会使树脂失效等,所以,随之而来的是化学法、电解法等逐渐出现并得到应用,化学法的不足之处是在于占地面积较大,产生含重金属污泥,污泥没有得到妥善的处理,所以存在二次污染问题。电解法的不足之处在于耗电高,重金属含量较高时使用效果不理想,电解法常用于贵重金属的回收,而对于回收价值不高的金属,比如说铜,那就得不偿失。环境工作者很早就提出有可能利用生物法去除重金属,并进行了多年的研究。目前广泛采用的都是菌种接种到液体培养基中,在一定的温度以及转速的培养条件下,摇瓶培养出菌丝球,再经过洗涤、过滤、烘干、磨碎和过筛之后才成为可用的吸附剂,虽然绿色环保,可其繁琐的操作步骤、昂贵的培养基费用和苛刻的培养条件使其难于实现工业化。Traditional heavy metal removal technology: The traditional methods for the removal of heavy metals include chemical precipitation, redox, ion exchange, electrochemical treatment, filtration, reverse osmosis, solvent extraction and evaporation recovery. Various physical and chemical methods are only the transfer, concentration, or change of the form of heavy metal ions. Heavy metals will not disappear and the total amount will not decrease. This is what distinguishes heavy metal wastewater from other wastewater. In the early years, the ion exchange method was widely used, but due to the high cost of the resin, there are certain restrictions on the original water quality, such as organic matter and oxides in the wastewater will cause the resin to fail, so the chemical method followed. , electrolysis, etc. have gradually appeared and been applied. The disadvantage of the chemical method is that it occupies a large area and produces sludge containing heavy metals. The sludge has not been properly treated, so there is a problem of secondary pollution. The disadvantage of the electrolysis method is that it consumes a lot of electricity, and the use effect is not ideal when the content of heavy metals is high. The electrolysis method is often used for the recovery of precious metals, but for metals with low recovery value, such as copper, the loss outweighs the gain. Environmental workers have long proposed that it is possible to use biological methods to remove heavy metals, and have conducted research for many years. What is widely used at present is to inoculate the bacteria into the liquid culture medium. Under the culture conditions of certain temperature and rotating speed, the mycelial balls are cultivated in the shaking flask, and then washed, filtered, dried, ground and sieved before being washed. As an available adsorbent, although it is green and environmentally friendly, its cumbersome operation steps, expensive medium costs and harsh culture conditions make it difficult to realize industrialization.
发明内容Contents of the invention
本发明的目的是要解决现有霉菌菌丝球粉末吸附剂吸附效果差以及成本高的问题,而提供的一种利用霉菌孢子吸附废水中重金属的方法。The purpose of the present invention is to solve the problems of poor adsorption effect and high cost of the existing mold mycelium ball powder adsorbent, and provide a method for using mold spores to adsorb heavy metals in waste water.
本发明一种利用霉菌孢子吸附废水中重金属的方法是按照以下步骤制备的:A method of utilizing mold spores to adsorb heavy metals in waste water of the present invention is prepared according to the following steps:
一、将霉菌孢子接种于固体培养基上,在29~31℃的条件下培养,然后收集霉菌气生菌丝上自然脱落的霉菌孢子;1. Inoculate the mold spores on a solid medium, cultivate them at 29-31°C, and then collect the mold spores that naturally fall off from the aerial hyphae of the mold;
二、将步骤一收集的霉菌孢子投加到含重金属的废水中,然后在温度为10~40℃的条件下进行搅拌,吸附1.5~2.5h,即完成;其中霉菌为菌株号98003的黑曲霉;霉菌孢子与含重金属的废水的质量体积比为1:(900~1100)g/mL。2. Add the mold spores collected in step 1 to the wastewater containing heavy metals, then stir at a temperature of 10-40°C, and complete the adsorption for 1.5-2.5 hours; the mold is Aspergillus niger with strain number 98003 ; The mass volume ratio of mold spores to wastewater containing heavy metals is 1: (900-1100) g/mL.
本发明的优点是孢子的收集可以简化吸附剂制备步骤,节约成本的同时提高重金属吸附量。孢子是霉菌在固体培养基表面生长后期由分化的气生菌丝繁殖而来,大约7天后可自行脱落,孢子是一种抗逆性极强的休眠体,它的抗物理化学及药物的作用很强,所以即使在吸附过程中细胞壁也不容易被破坏,同时孢子的直径很小,大约为2um,因此具有较大的比表面面积。The invention has the advantages that the collection of spores can simplify the preparation steps of the adsorbent, save the cost and increase the heavy metal adsorption capacity at the same time. The spore is the fungus that propagates from the differentiated aerial hyphae in the late stage of growth on the surface of the solid medium, and it can fall off by itself after about 7 days. The spore is a dormant body with strong stress resistance, and its resistance to physical, chemical and drug effects It is very strong, so the cell wall is not easily damaged even during the adsorption process. At the same time, the diameter of the spore is very small, about 2um, so it has a large specific surface area.
具体实施方式Detailed ways
具体实施方式一:本实施方式一种利用霉菌孢子吸附废水中重金属的方法是按照以下步骤制备的:Specific embodiment one: In this embodiment, a method for utilizing mold spores to adsorb heavy metals in wastewater is prepared according to the following steps:
一、将霉菌孢子接种于固体培养基上,在29~31℃的条件下培养,然后收集霉菌气生菌丝上自然脱落的霉菌孢子;1. Inoculate the mold spores on a solid medium, cultivate them at 29-31°C, and then collect the mold spores that naturally fall off from the aerial hyphae of the mold;
二、将步骤一收集的霉菌孢子投加到含重金属的废水中,然后在温度为10~40℃的条件下进行搅拌,吸附1.5~2.5h,即完成;霉菌孢子与含重金属的废水的质量体积比为1:(900~1100)g/mL。2. Add the mold spores collected in step 1 to the wastewater containing heavy metals, then stir at a temperature of 10-40°C, and complete the adsorption for 1.5-2.5 hours; the quality of mold spores and wastewater containing heavy metals The volume ratio is 1: (900~1100) g/mL.
其中本实施方式中的霉菌为菌株号98003的黑曲霉,购买自哈尔滨春瑞科技开发有限公司。The mold in this embodiment is Aspergillus niger with strain number 98003, purchased from Harbin Chunrui Technology Development Co., Ltd.
本实施方式的优点是孢子的收集可以简化吸附剂制备步骤,节约成本的同时提高重金属吸附量。The advantage of this embodiment is that the collection of spores can simplify the preparation steps of the adsorbent, save costs and increase the adsorption capacity of heavy metals.
具体实施方式二:本实施方式与具体实施方式一不同的是:所述的霉菌为菌株号98003的黑曲霉(Aspergillus niger)。其他与具体实施方式一相同。Specific embodiment two: the difference between this embodiment and specific embodiment one is: the mold is Aspergillus niger (Aspergillus niger) with strain number 98003. Others are the same as the first embodiment.
具体实施方式三:本实施方式与具体实施方式一或二不同的是:步骤一中所述的固体培养基为改良马丁培养基、PDA培养基或干稻草培养基。其他与具体实施方式一或二相同。Specific embodiment three: the difference between this embodiment and specific embodiment one or two is that: the solid medium described in step one is improved Martin medium, PDA medium or dry rice straw medium. Others are the same as those in Embodiment 1 or 2.
本实施方式改良马丁培养基:蛋白胨5.0g、磷酸氢二钾1.0g、酵母浸出粉2.0g、硫酸镁0.5g、葡萄糖20.0g、琼脂粉15g、水1000ml,ph6.4;The present embodiment improves Martin medium: peptone 5.0g, dipotassium hydrogen phosphate 1.0g, yeast extract powder 2.0g, magnesium sulfate 0.5g, glucose 20.0g, agar powder 15g, water 1000ml, ph6.4;
PDA培养基:200g去皮马铃薯,水煮30min后,蒸馏水补足1000ml,加入20g葡萄糖,琼脂粉15g;PDA medium: 200g peeled potatoes, boiled in water for 30min, supplemented with 1000ml of distilled water, added 20g of glucose, 15g of agar powder;
干稻草培养基:干稻草磨碎过60目筛,以质量体积比1:1加入清水。Dry straw medium: Grind dry straw through a 60-mesh sieve, and add water at a mass-volume ratio of 1:1.
具体实施方式四:本实施方式与具体实施方式一至三之一不同的是:步骤二中所述的重金属铜。其他步骤和参数与具体实施方式一至三之一相同。Embodiment 4: This embodiment differs from Embodiment 1 to Embodiment 3 in that: the heavy metal copper described in step 2. Other steps and parameters are the same as those in the first to third specific embodiments.
具体实施方式五:本实施方式与具体实施方式一至四之一不同的是:步骤二中所述的在温度为30℃的条件下进行搅拌。其他步骤和参数与具体实施方式一至四之一相同。Embodiment 5: This embodiment is different from Embodiment 1 to Embodiment 4 in that: Stirring is carried out at a temperature of 30° C. as described in Step 2. Other steps and parameters are the same as one of the specific embodiments 1 to 4.
具体实施方式六:本实施方式与具体实施方式一至五之一不同的是:步骤二中所述的搅拌速度为0~300rmp。其他步骤和参数与具体实施方式一至五之一相同。Embodiment 6: This embodiment differs from Embodiment 1 to Embodiment 5 in that: the stirring speed in step 2 is 0-300 rpm. Other steps and parameters are the same as one of the specific embodiments 1 to 5.
具体实施方式七:本实施方式与具体实施方式一至六之一不同的是:吸附时间为2h。其他步骤和参数与具体实施方式一至六之一相同。Embodiment 7: The difference between this embodiment and one of Embodiments 1 to 6 is that the adsorption time is 2 hours. Other steps and parameters are the same as one of the specific embodiments 1 to 6.
通过以下试验验证本发明的有益效果:Prove the beneficial effect of the present invention by following test:
试验1、本试验试验组利用霉菌孢子吸附废水中重金属的方法是按照以下步骤制备的:Test 1, the method that this test test group utilizes mold spores to adsorb heavy metals in wastewater is prepared according to the following steps:
一、将霉菌孢子接种于改良马丁培养基上,在30℃的条件下培养6~7天,然后收集霉菌气生菌丝上自然脱落的霉菌孢子;1. Inoculate the mold spores on the improved Martin medium, culture them at 30°C for 6-7 days, and then collect the mold spores that naturally fall off from the aerial hyphae of the mold;
二、将步骤一收集的霉菌孢子投加到铜含量为30mg/L的废水中,然后在温度为30℃的条件下进行搅拌,搅拌速度为100rmp,吸附2h,即完成;其中霉菌的具体菌株名称及拉丁文;霉菌孢子与含铜废水的质量体积比为1:1000g/mL。2. Add the mold spores collected in step 1 to the wastewater with a copper content of 30mg/L, and then stir at a temperature of 30°C at a stirring speed of 100rmp, and the adsorption is complete for 2 hours; the specific strain of the mold Name and Latin; the mass volume ratio of mold spores to copper-containing wastewater is 1:1000g/mL.
试验组孢子的吸附量为27.2mg/g。The adsorption capacity of spores in the test group was 27.2 mg/g.
对照组将霉菌菌丝球粉末吸附剂投加到铜含量为30mg/L的废水中,然后在温度为30℃的条件下进行搅拌,搅拌速度为100rmp,吸附2h,即完成;其中霉菌的具体菌株名称及拉丁文;霉菌菌丝球粉末吸附剂与含重铜废水的质量体积比为1:1000g/mL。In the control group, the mold mycelium ball powder adsorbent was added to the wastewater with a copper content of 30mg/L, and then stirred at a temperature of 30°C, the stirring speed was 100rmp, and the adsorption was completed for 2 hours; the specific content of the mold Strain name and Latin; the mass volume ratio of mold mycelium ball powder adsorbent to heavy copper-containing wastewater is 1:1000g/mL.
其中霉菌菌丝球粉末吸附剂的制备方法为:将霉菌接种到液体培养基中,在30℃以及转速为100rmp的培养条件下,摇瓶培养出菌丝球,再经过洗涤、过滤、烘干、磨碎和过筛之后即得到霉菌菌丝球粉末吸附剂。对照组霉菌菌丝球粉末吸附剂吸附量为5.7mg/g。The preparation method of the mold mycelium ball powder adsorbent is as follows: inoculate the mold into the liquid medium, and under the culture conditions of 30°C and the rotation speed of 100rmp, shake the flask to cultivate the mycelium ball, and then wash, filter, and dry , after grinding and sieving, the mold mycelia ball powder adsorbent is obtained. The adsorption capacity of the mold mycelium ball powder adsorbent in the control group was 5.7 mg/g.
本试验试验组可以简化吸附剂制备步骤,节约成本的同时提高重金属吸附量。The experimental group can simplify the preparation steps of the adsorbent, save the cost and increase the adsorption capacity of heavy metals at the same time.
试验2、本试验试验组利用霉菌孢子吸附废水中重金属的方法是按照以下步骤制备的:Test 2, the method that this test test group utilizes mold spores to adsorb heavy metals in wastewater is prepared according to the following steps:
一、将霉菌孢子接种于改良马丁培养基上,在30℃的条件下培养7天,然后收集霉菌气生菌丝上自然脱落的霉菌孢子;1. Inoculate the mold spores on the improved Martin medium, culture them at 30°C for 7 days, and then collect the mold spores that naturally fall off from the aerial hyphae of the mold;
二、将步骤一收集的霉菌孢子投加到铜含量为30mg/L的废水中,然后在温度为30℃的条件下进行吸附,吸附2h,搅拌速度为0rmp,即完成;其中霉菌的具体菌株名称及拉丁文;霉菌孢子与含铜废水的质量体积比为1:1000g/mL。2. Add the mold spores collected in step 1 to the wastewater with a copper content of 30mg/L, and then perform adsorption at a temperature of 30°C for 2 hours, and the stirring speed is 0rmp, which is completed; the specific strain of the mold Name and Latin; the mass volume ratio of mold spores to copper-containing wastewater is 1:1000g/mL.
试验组孢子的吸附量为24.5mg/g。The adsorption capacity of spores in the test group was 24.5 mg/g.
试验1~2中的霉菌为菌株号98003的黑曲霉,购买自哈尔滨春瑞科技开发有限公司。The mold in Tests 1-2 was Aspergillus niger with strain number 98003, which was purchased from Harbin Chunrui Technology Development Co., Ltd.
Claims (7)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201510226403.2A CN104787902A (en) | 2015-05-06 | 2015-05-06 | Method for adsorbing heavy metal in wastewater by using mold spore |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201510226403.2A CN104787902A (en) | 2015-05-06 | 2015-05-06 | Method for adsorbing heavy metal in wastewater by using mold spore |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN104787902A true CN104787902A (en) | 2015-07-22 |
Family
ID=53553154
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201510226403.2A Pending CN104787902A (en) | 2015-05-06 | 2015-05-06 | Method for adsorbing heavy metal in wastewater by using mold spore |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN104787902A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN118993350A (en) * | 2024-08-20 | 2024-11-22 | 清华大学 | Method for adsorbing and recovering precious metals in aqueous sample |
Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US4732681A (en) * | 1985-05-02 | 1988-03-22 | Ramot University Authority For Applied Research And Industrial Development Ltd. | Removal of contaminants |
| CN103525870A (en) * | 2013-10-23 | 2014-01-22 | 嘉兴学院 | Microbial flocculant as well as preparation method and application thereof |
| CN104261564A (en) * | 2014-10-14 | 2015-01-07 | 南华大学 | Method for repairing low-concentration uranium polluted water by utilizing syngonium podophyllum-aspergillus niger symbiotic system |
| CN104386832A (en) * | 2014-12-05 | 2015-03-04 | 河南省科学院生物研究所有限责任公司 | Method for processing leaded wastewater by using microbial bacteria |
-
2015
- 2015-05-06 CN CN201510226403.2A patent/CN104787902A/en active Pending
Patent Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US4732681A (en) * | 1985-05-02 | 1988-03-22 | Ramot University Authority For Applied Research And Industrial Development Ltd. | Removal of contaminants |
| CN103525870A (en) * | 2013-10-23 | 2014-01-22 | 嘉兴学院 | Microbial flocculant as well as preparation method and application thereof |
| CN104261564A (en) * | 2014-10-14 | 2015-01-07 | 南华大学 | Method for repairing low-concentration uranium polluted water by utilizing syngonium podophyllum-aspergillus niger symbiotic system |
| CN104386832A (en) * | 2014-12-05 | 2015-03-04 | 河南省科学院生物研究所有限责任公司 | Method for processing leaded wastewater by using microbial bacteria |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN118993350A (en) * | 2024-08-20 | 2024-11-22 | 清华大学 | Method for adsorbing and recovering precious metals in aqueous sample |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN108715843B (en) | Preparation method of immobilized cell ball for treating heavy metal wastewater | |
| CN101733074B (en) | Method for preparing film type biological adsorbing medium | |
| CN112538449B (en) | A strain of Alcaligenes faecalis DY-8 and its application in removing heavy metal cadmium | |
| CN102989427B (en) | Enteromorpha absorbent and preparation technology thereof | |
| CN112831422B (en) | A kind of manganese oxidizing fungus and its application | |
| CN104226259A (en) | Threonine modified attapulgite adsorbent and application thereof | |
| CN103451103B (en) | High-cadmium-adsorption filamentous fungus Paecilomyces lilacinus XLA, and preparation method and application thereof | |
| CN106190871B (en) | Method for treating heavy metal contaminated soil by bioleaching with composite filamentous fungi by taking straws as carbon source | |
| CN104689788A (en) | Biochar modification method for improving ammonium nitrogen adsorption capability in soil/water | |
| CN104531537A (en) | Aspergillus flavus bacterial strain and application thereof | |
| CN103740623B (en) | One plant height effect removes Pseudoalteromonas and the application thereof of cadmium and phosphorus in waste water | |
| CN103451105B (en) | A kind of filamentous fungus Penicllium chrysogenum J-5 of high absorption cadmium and preparation method and application | |
| CN104801285A (en) | Preparation method of mycete and agricultural and forestry waste mixed bio-adsorbent | |
| CN108359610B (en) | Facultative marine fungal remediation agent modified by bisamidoxime base and method for remediation of uranium-contaminated water bodies | |
| CN102127517A (en) | Strain with heavy metal tolerance and applications thereof | |
| CN108311118A (en) | A kind of preparation method of modified synthesis zeolite heavy metal ion adsorbing material | |
| CN104787902A (en) | Method for adsorbing heavy metal in wastewater by using mold spore | |
| CN107236864A (en) | The method for extracting rare precious metals from flyash using Microorganism Leaching | |
| CN104176835A (en) | Method for repairing uranium (VI) polluted water body by using fungi treated by nonionic surfactant | |
| CN107881115B (en) | A kind of Anabaena and its application in removing cadmium in the environment | |
| CN104817243A (en) | Bioleaching-Fenton-like oxidation combined bottom mud heavy metal removal and dehydration method | |
| CN108636372A (en) | A kind of aerobic particle mud-Fe3O4The preparation and application of humic acid composite biological adsorption | |
| CN104163502B (en) | A method for remediating thorium(IV) polluted water by living facultative marine fungi | |
| CN103451104B (en) | High-cadmium-adsorption filamentous fungi hair mold XLC as well as preparation method and application thereof | |
| CN103710267B (en) | A kind of long shoot mould M-04 of wood and application thereof |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C06 | Publication | ||
| PB01 | Publication | ||
| EXSB | Decision made by sipo to initiate substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| RJ01 | Rejection of invention patent application after publication | ||
| RJ01 | Rejection of invention patent application after publication |
Application publication date: 20150722 |