CN107308918A - A kind of preparation method of rich nitride polyporous material and its in retrieving circuit board noble metal application - Google Patents
A kind of preparation method of rich nitride polyporous material and its in retrieving circuit board noble metal application Download PDFInfo
- Publication number
- CN107308918A CN107308918A CN201710574514.1A CN201710574514A CN107308918A CN 107308918 A CN107308918 A CN 107308918A CN 201710574514 A CN201710574514 A CN 201710574514A CN 107308918 A CN107308918 A CN 107308918A
- Authority
- CN
- China
- Prior art keywords
- rich nitride
- waste
- polyporous material
- recycling
- hours
- 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
- 239000000463 material Substances 0.000 title claims abstract description 27
- 238000002360 preparation method Methods 0.000 title claims abstract description 6
- 229910000510 noble metal Inorganic materials 0.000 title claims description 10
- 150000004767 nitrides Chemical class 0.000 title claims 9
- LYCAIKOWRPUZTN-UHFFFAOYSA-N Ethylene glycol Chemical compound OCCO LYCAIKOWRPUZTN-UHFFFAOYSA-N 0.000 claims abstract description 39
- AZQWKYJCGOJGHM-UHFFFAOYSA-N 1,4-benzoquinone Chemical compound O=C1C=CC(=O)C=C1 AZQWKYJCGOJGHM-UHFFFAOYSA-N 0.000 claims abstract description 34
- CTQNGGLPUBDAKN-UHFFFAOYSA-N O-Xylene Chemical compound CC1=CC=CC=C1C CTQNGGLPUBDAKN-UHFFFAOYSA-N 0.000 claims abstract description 18
- 229920000877 Melamine resin Polymers 0.000 claims abstract description 17
- JDSHMPZPIAZGSV-UHFFFAOYSA-N melamine Chemical compound NC1=NC(N)=NC(N)=N1 JDSHMPZPIAZGSV-UHFFFAOYSA-N 0.000 claims abstract description 17
- 239000011148 porous material Substances 0.000 claims abstract description 17
- 239000008096 xylene Substances 0.000 claims abstract description 14
- 230000018044 dehydration Effects 0.000 claims abstract description 6
- 238000006297 dehydration reaction Methods 0.000 claims abstract description 6
- 239000002904 solvent Substances 0.000 claims abstract description 5
- 238000011084 recovery Methods 0.000 claims description 10
- 238000006068 polycondensation reaction Methods 0.000 claims description 4
- 238000009835 boiling Methods 0.000 claims description 3
- 229940005561 1,4-benzoquinone Drugs 0.000 claims 2
- 150000001412 amines Chemical class 0.000 claims 1
- UMGDCJDMYOKAJW-UHFFFAOYSA-N thiourea Chemical compound NC(N)=S UMGDCJDMYOKAJW-UHFFFAOYSA-N 0.000 abstract description 38
- 239000010970 precious metal Substances 0.000 abstract description 37
- 239000010793 electronic waste Substances 0.000 abstract description 24
- 238000001179 sorption measurement Methods 0.000 abstract description 22
- XSQUKJJJFZCRTK-UHFFFAOYSA-N Urea Natural products NC(N)=O XSQUKJJJFZCRTK-UHFFFAOYSA-N 0.000 abstract description 19
- 238000004064 recycling Methods 0.000 abstract description 16
- 239000002699 waste material Substances 0.000 abstract description 14
- 238000002386 leaching Methods 0.000 abstract description 11
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 abstract description 10
- 239000007788 liquid Substances 0.000 abstract description 5
- 229910052757 nitrogen Inorganic materials 0.000 abstract description 5
- 239000004033 plastic Substances 0.000 abstract description 5
- 229920003023 plastic Polymers 0.000 abstract description 5
- 238000010438 heat treatment Methods 0.000 abstract description 4
- 102100025912 Melanopsin Human genes 0.000 abstract 1
- 239000013213 metal-organic polyhedra Substances 0.000 abstract 1
- 238000012011 method of payment Methods 0.000 abstract 1
- YXFVVABEGXRONW-UHFFFAOYSA-N Toluene Chemical compound CC1=CC=CC=C1 YXFVVABEGXRONW-UHFFFAOYSA-N 0.000 description 27
- 238000000034 method Methods 0.000 description 21
- 239000000243 solution Substances 0.000 description 21
- 238000003756 stirring Methods 0.000 description 21
- 238000005516 engineering process Methods 0.000 description 19
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 description 18
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 17
- 229910052751 metal Inorganic materials 0.000 description 13
- 239000002184 metal Substances 0.000 description 13
- 229910052737 gold Inorganic materials 0.000 description 12
- 239000010931 gold Substances 0.000 description 12
- 239000007787 solid Substances 0.000 description 10
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 9
- 239000002244 precipitate Substances 0.000 description 9
- -1 gold ions Chemical class 0.000 description 8
- 238000001479 atomic absorption spectroscopy Methods 0.000 description 7
- PCHJSUWPFVWCPO-UHFFFAOYSA-N gold Chemical compound [Au] PCHJSUWPFVWCPO-UHFFFAOYSA-N 0.000 description 7
- 238000011160 research Methods 0.000 description 7
- 238000000605 extraction Methods 0.000 description 6
- 238000000926 separation method Methods 0.000 description 6
- 229910052709 silver Inorganic materials 0.000 description 6
- 238000006243 chemical reaction Methods 0.000 description 5
- 230000007613 environmental effect Effects 0.000 description 5
- 238000009854 hydrometallurgy Methods 0.000 description 5
- 150000002500 ions Chemical class 0.000 description 5
- 150000002739 metals Chemical class 0.000 description 5
- 239000004332 silver Substances 0.000 description 5
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 description 4
- 239000007864 aqueous solution Substances 0.000 description 4
- 239000008139 complexing agent Substances 0.000 description 4
- DAFYMZZLYPHPNG-UHFFFAOYSA-N gold;thiourea Chemical compound [Au].NC(N)=S DAFYMZZLYPHPNG-UHFFFAOYSA-N 0.000 description 4
- 229910017604 nitric acid Inorganic materials 0.000 description 4
- 230000001590 oxidative effect Effects 0.000 description 4
- 230000002378 acidificating effect Effects 0.000 description 3
- 230000015572 biosynthetic process Effects 0.000 description 3
- 229910052802 copper Inorganic materials 0.000 description 3
- 239000010949 copper Substances 0.000 description 3
- 238000010828 elution Methods 0.000 description 3
- 238000002474 experimental method Methods 0.000 description 3
- 238000005342 ion exchange Methods 0.000 description 3
- 239000007800 oxidant agent Substances 0.000 description 3
- 239000002893 slag Substances 0.000 description 3
- 238000000638 solvent extraction Methods 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 238000003786 synthesis reaction Methods 0.000 description 3
- 239000002351 wastewater Substances 0.000 description 3
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 description 2
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 description 2
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 2
- FOIXSVOLVBLSDH-UHFFFAOYSA-N Silver ion Chemical compound [Ag+] FOIXSVOLVBLSDH-UHFFFAOYSA-N 0.000 description 2
- ZMZDMBWJUHKJPS-UHFFFAOYSA-M Thiocyanate anion Chemical compound [S-]C#N ZMZDMBWJUHKJPS-UHFFFAOYSA-M 0.000 description 2
- 239000011358 absorbing material Substances 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 2
- 238000011161 development Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000003912 environmental pollution Methods 0.000 description 2
- ZMZDMBWJUHKJPS-UHFFFAOYSA-N hydrogen thiocyanate Natural products SC#N ZMZDMBWJUHKJPS-UHFFFAOYSA-N 0.000 description 2
- 238000009776 industrial production Methods 0.000 description 2
- NUJOXMJBOLGQSY-UHFFFAOYSA-N manganese dioxide Chemical compound O=[Mn]=O NUJOXMJBOLGQSY-UHFFFAOYSA-N 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 229910052755 nonmetal Inorganic materials 0.000 description 2
- 238000002414 normal-phase solid-phase extraction Methods 0.000 description 2
- 239000003960 organic solvent Substances 0.000 description 2
- 230000000704 physical effect Effects 0.000 description 2
- 238000009853 pyrometallurgy Methods 0.000 description 2
- 239000002994 raw material Substances 0.000 description 2
- 230000035484 reaction time Effects 0.000 description 2
- 238000007670 refining Methods 0.000 description 2
- 229920005989 resin Polymers 0.000 description 2
- 239000011347 resin Substances 0.000 description 2
- WKBOTKDWSSQWDR-UHFFFAOYSA-N Bromine atom Chemical compound [Br] WKBOTKDWSSQWDR-UHFFFAOYSA-N 0.000 description 1
- XFXPMWWXUTWYJX-UHFFFAOYSA-N Cyanide Chemical compound N#[C-] XFXPMWWXUTWYJX-UHFFFAOYSA-N 0.000 description 1
- VTLYFUHAOXGGBS-UHFFFAOYSA-N Fe3+ Chemical compound [Fe+3] VTLYFUHAOXGGBS-UHFFFAOYSA-N 0.000 description 1
- BQCADISMDOOEFD-UHFFFAOYSA-N Silver Chemical compound [Ag] BQCADISMDOOEFD-UHFFFAOYSA-N 0.000 description 1
- 238000003723 Smelting Methods 0.000 description 1
- ATJFFYVFTNAWJD-UHFFFAOYSA-N Tin Chemical compound [Sn] ATJFFYVFTNAWJD-UHFFFAOYSA-N 0.000 description 1
- 229910052782 aluminium Inorganic materials 0.000 description 1
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 1
- SOIFLUNRINLCBN-UHFFFAOYSA-N ammonium thiocyanate Chemical compound [NH4+].[S-]C#N SOIFLUNRINLCBN-UHFFFAOYSA-N 0.000 description 1
- 238000004458 analytical method Methods 0.000 description 1
- QZPSXPBJTPJTSZ-UHFFFAOYSA-N aqua regia Chemical compound Cl.O[N+]([O-])=O QZPSXPBJTPJTSZ-UHFFFAOYSA-N 0.000 description 1
- GDTBXPJZTBHREO-UHFFFAOYSA-N bromine Substances BrBr GDTBXPJZTBHREO-UHFFFAOYSA-N 0.000 description 1
- 229910052794 bromium Inorganic materials 0.000 description 1
- 239000006227 byproduct Substances 0.000 description 1
- 239000003054 catalyst Substances 0.000 description 1
- 239000000919 ceramic Substances 0.000 description 1
- 230000007797 corrosion Effects 0.000 description 1
- 238000005260 corrosion Methods 0.000 description 1
- 230000007547 defect Effects 0.000 description 1
- 238000003795 desorption Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 150000002013 dioxins Chemical class 0.000 description 1
- 239000003814 drug Substances 0.000 description 1
- 238000010891 electric arc Methods 0.000 description 1
- 239000003063 flame retardant Substances 0.000 description 1
- 239000012530 fluid Substances 0.000 description 1
- 238000010574 gas phase reaction Methods 0.000 description 1
- 239000003365 glass fiber Substances 0.000 description 1
- 150000004820 halides Chemical class 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- 238000007654 immersion Methods 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 238000002329 infrared spectrum Methods 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- JEIPFZHSYJVQDO-UHFFFAOYSA-N iron(III) oxide Inorganic materials O=[Fe]O[Fe]=O JEIPFZHSYJVQDO-UHFFFAOYSA-N 0.000 description 1
- 238000000622 liquid--liquid extraction Methods 0.000 description 1
- 238000002844 melting Methods 0.000 description 1
- 230000008018 melting Effects 0.000 description 1
- 229910021645 metal ion Inorganic materials 0.000 description 1
- 238000010310 metallurgical process Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 239000012071 phase Substances 0.000 description 1
- 238000002203 pretreatment Methods 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
- 239000010944 silver (metal) Substances 0.000 description 1
- 238000011172 small scale experimental method Methods 0.000 description 1
- 239000007790 solid phase Substances 0.000 description 1
- 238000003860 storage Methods 0.000 description 1
- DHCDFWKWKRSZHF-UHFFFAOYSA-N sulfurothioic S-acid Chemical compound OS(O)(=O)=S DHCDFWKWKRSZHF-UHFFFAOYSA-N 0.000 description 1
- 238000001308 synthesis method Methods 0.000 description 1
- 238000012360 testing method Methods 0.000 description 1
- 229910052718 tin Inorganic materials 0.000 description 1
- 239000002341 toxic gas Substances 0.000 description 1
- 230000001988 toxicity Effects 0.000 description 1
- 231100000419 toxicity Toxicity 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/22—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
- B01J20/26—Synthetic macromolecular compounds
- B01J20/262—Synthetic macromolecular compounds obtained otherwise than by reactions only involving carbon to carbon unsaturated bonds, e.g. obtained by polycondensation
-
- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B11/00—Obtaining noble metals
- C22B11/04—Obtaining noble metals by wet processes
- C22B11/042—Recovery of noble metals from waste materials
- C22B11/046—Recovery of noble metals from waste materials from manufactured products, e.g. from printed circuit boards, from photographic films, paper or baths
-
- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B3/00—Extraction of metal compounds from ores or concentrates by wet processes
- C22B3/20—Treatment or purification of solutions, e.g. obtained by leaching
- C22B3/22—Treatment or purification of solutions, e.g. obtained by leaching by physical processes, e.g. by filtration, by magnetic means, or by thermal decomposition
- C22B3/24—Treatment or purification of solutions, e.g. obtained by leaching by physical processes, e.g. by filtration, by magnetic means, or by thermal decomposition by adsorption on solid substances, e.g. by extraction with solid resins
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P10/00—Technologies related to metal processing
- Y02P10/20—Recycling
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Organic Chemistry (AREA)
- Mechanical Engineering (AREA)
- Manufacturing & Machinery (AREA)
- Materials Engineering (AREA)
- Metallurgy (AREA)
- Geology (AREA)
- Geochemistry & Mineralogy (AREA)
- General Life Sciences & Earth Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Analytical Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Manufacture And Refinement Of Metals (AREA)
Abstract
本发明涉及一种富氮多孔材料的制备方法及其在回收电路板中贵金属的应用,以乙二醇为溶剂,加入三聚氰胺和对苯醌,加热缩聚,最后加入二甲苯脱水,得到多孔材料MOPs‑1。本发明提供一种高效贵金属吸附材料MOPs‑1,以硫脲浸出液为废电路板处理液,研究多孔材料的功能,能够高效吸附硫脲溶液中贵金属,使硫脲溶液重复使用,从而达到电子废弃物的资源化,回收电子废弃物中的贵金属,并再生塑料,保护环境,产生经济和社会效益。
The invention relates to a preparation method of a nitrogen-rich porous material and its application in recycling precious metals in circuit boards. Using ethylene glycol as a solvent, adding melamine and p-benzoquinone, heating and polycondensing, and finally adding xylene for dehydration to obtain porous material MOPs -1. The invention provides a high-efficiency precious metal adsorption material MOPs-1, which uses thiourea leaching solution as waste circuit board treatment liquid, studies the function of porous materials, can efficiently adsorb precious metals in thiourea solution, and reuses thiourea solution to achieve electronic waste Recycling of materials, recycling precious metals in electronic waste, and recycling plastics, protecting the environment, and generating economic and social benefits.
Description
技术领域technical field
本发明涉及新型多孔材料领域,具体涉及一种富氮多孔材料的制备方法及其在回收电路板中贵金属的应用。The invention relates to the field of novel porous materials, in particular to a preparation method of a nitrogen-rich porous material and its application in recycling circuit boards of precious metals.
背景技术Background technique
2016年,全世界产生高达5000万吨的废电器。据联合国环境规划署报告,中国是第二大电子垃圾产生国,每年的电子垃圾超过230万吨,仅次于美国的300万吨。全球每年约3.5亿吨电子垃圾通过各种途径流入中国。这些电子垃圾如果不进行处理,不仅对环境造成严重的影响,而且也会造成严重的资源浪费。据统计,平均1吨普通的电子废弃物含有490kg金属,4kg电线,12kg电路板等。如不进行回收利用,将会造成资源的巨大浪费。因此,随着电子废弃物对生态环境的影响日益凸现,以及电子废弃物自身的巨大经济价值,电子废弃物的资源化回收正在成为一个全球性的课题。In 2016, the world produced up to 50 million tons of waste electrical appliances. According to the United Nations Environment Program report, China is the second largest producer of e-waste, with more than 2.3 million tons of e-waste per year, second only to the 3 million tons of the United States. About 350 million tons of e-waste flows into China through various channels around the world every year. If these electronic wastes are not treated, they will not only have a serious impact on the environment, but also cause a serious waste of resources. According to statistics, an average of 1 ton of ordinary electronic waste contains 490kg of metal, 4kg of wires, 12kg of circuit boards, etc. If it is not recycled, it will cause a huge waste of resources. Therefore, with the increasing impact of e-waste on the ecological environment and the huge economic value of e-waste itself, the resource recovery of e-waste is becoming a global issue.
相对于塑料或其它组分的资源化再利用,金属资源再利用在技术和经济方面具有明显的优势。贵金属由于其优良的导电性和抗腐蚀性能,被用于电子产品,占电子废弃物价值的绝大部分,是电子废弃物回收的主要经济价值。使用有效方法资源化电脑、手机等电子废弃物不但可以缓解环境压力,而且可以回收Ag、Au、Cu等贵金属,缓解世界资源日益枯竭的压力。Compared with the recycling of plastics or other components, the recycling of metal resources has obvious advantages in terms of technology and economy. Due to their excellent electrical conductivity and corrosion resistance, precious metals are used in electronic products, accounting for the vast majority of the value of e-waste, and are the main economic value of e-waste recycling. Using effective methods to recycle electronic waste such as computers and mobile phones can not only relieve environmental pressure, but also recycle precious metals such as Ag, Au, and Cu, alleviating the pressure of the world's increasingly depleted resources.
电子废弃物中贵金属回收的研究现状:20世纪80年代以来,西方国家以二次资源形式供给的贵金属逐年递增,仅1998年以二次资源形式供给的金就高达1089吨,约为当年矿产金的43%。由此可见,贵金属的回收已逐步引起了人们的重视。目前回收贵金属的技术主要有:火法冶金技术、湿法冶金技术、生物冶金技术。Research status of precious metal recovery from electronic waste: Since the 1980s, the supply of precious metals in the form of secondary resources in Western countries has increased year by year. In 1998 alone, the supply of gold in the form of secondary resources was as high as 1,089 tons, about 43% of. It can be seen that the recovery of precious metals has gradually attracted people's attention. At present, the technologies for recycling precious metals mainly include: pyrometallurgy technology, hydrometallurgy technology, and biometallurgy technology.
火法冶金技术。火法冶金技术一般包括焙烧、电弧炉或鼓风炉溶炼、高温气相反应等。在高温下将电子废弃物进行熔炼,使非金属与金属分离,贵金属富集于金属相或锍中从而与其它金属分离,再通过电解精炼或火法精炼得到贵金属。Pyrometallurgical technology. Pyrometallurgical technology generally includes roasting, electric arc furnace or blast furnace melting, high temperature gas phase reaction, etc. The electronic waste is smelted at high temperature to separate the non-metal from the metal, and the precious metal is enriched in the metal phase or matte to separate from other metals, and then the precious metal is obtained by electrolytic refining or pyro-refining.
火法冶金处理电子废弃物的技术也有一些缺陷主要有:①电子废弃物含有碳氟氯化合物、溴阻燃剂及有机物,在氧化条件下易生成二噁英等有毒气体,因此必须有严格高效的废气处理设备和技术,否则会造成严重的二次污染;②贵金属和铜能以较高回收率实现回收,但是铝、铁、锡等其它金属则被氧化而进入炉渣,从而难以回收;③电子废弃物中的陶瓷、玻璃纤维等也进入炉渣,这就极大增加了熔炼的出渣量,同时也增加了贵金属和其他金属的夹带损失。The technology of pyrometallurgical treatment of electronic waste also has some defects. The main ones are: ①Electronic waste contains chlorofluorocarbons, bromine flame retardants and organic substances, which are easy to generate toxic gases such as dioxins under oxidative conditions, so strict and efficient procedures must be carried out. Otherwise, it will cause serious secondary pollution; ②Precious metals and copper can be recovered at a relatively high recovery rate, but aluminum, iron, tin and other metals are oxidized and enter the slag, making it difficult to recycle; ③ Ceramics and glass fibers in electronic waste also enter the slag, which greatly increases the amount of slag produced during smelting, and also increases the entrainment loss of precious metals and other metals.
湿法冶金技术。相对于火法冶金技术回收电子废弃物来说,湿法冶金技术要更加复杂,工艺也更加多样化。湿法冶金技术一般包括两个步骤:用酸性或碱性等溶剂进行浸出,然后是浸出液的分离和除杂。此外,湿法回收电子废弃物的工业生产中,一般会有机械破碎等预处理。在采用湿法冶金工艺回收电子废弃物中的贵金属时,浸出过程通常采用的溶剂主要包括氰化物、卤化物、硫脲、硫代硫酸盐等,然后从浸出液中再通过多种方法提取其中的贵金属。目前常见的提取方法有:溶剂萃取法、离子交换、固相萃取-吸附法等。Hydrometallurgical technology. Compared with pyrometallurgical technology for recycling e-waste, hydrometallurgical technology is more complicated and the process is more diversified. Hydrometallurgy technology generally includes two steps: leaching with acidic or alkaline solvents, and then separation and removal of impurities from the leachate. In addition, in the industrial production of wet recycling of electronic waste, there are generally pretreatments such as mechanical crushing. When the hydrometallurgical process is used to recover precious metals in electronic waste, the solvents usually used in the leaching process mainly include cyanide, halide, thiourea, thiosulfate, etc., and then extract the precious metals from the leachate through various methods. precious metals. At present, the common extraction methods are: solvent extraction, ion exchange, solid phase extraction-adsorption and so on.
溶剂萃取法因其分离效果好,生产能力大,便于快速连续操作,过程中存储量小,较安全、易于实现自动控制等优点而被较多地应用,但萃取法要想得到更快的发展则主要依赖于高效、易得、成本低、损耗少的萃取剂的研制成功和合理使用。Solvent extraction method is widely used because of its good separation effect, large production capacity, convenient rapid and continuous operation, small storage capacity in the process, relatively safe, and easy to realize automatic control. However, the extraction method needs to be developed faster. It depends on the successful development and rational use of efficient, easy-to-obtain, low-cost, and less-loss extractants.
离子交换法因其合成方法简单,性能稳定,交换容量大,可重复使用等优点而被较多地应用。但对同种电荷离子和化学物理性能相似的离子的分离选择性不佳,吸附能力强树脂淋洗再生困难。因此,需进一步开发和改性树脂,优化、改进分离和淋洗工艺,以促进离子交换分离提纯贵金属技术较大的发展。The ion exchange method is widely used because of its simple synthesis method, stable performance, large exchange capacity, and reusability. However, the separation selectivity of ions with the same charge and similar chemical and physical properties is not good, and the resin with strong adsorption capacity is difficult to leaching and regenerate. Therefore, it is necessary to further develop and modify the resin, optimize and improve the separation and washing process, so as to promote the development of ion exchange separation and purification of precious metals.
与传统的液-液萃取技术相比,固相萃取法具有如下的优点:(1)操作步骤简单,分析速度快,缩短了预处理时间;(2)有机溶剂消耗量少,降低了实验成本,同时减少了对环境的污染。固相萃取法作为一种新型的样品前处理技术,已成为最为常用的分离富集方法,因此,近些年得到很快发展,并广泛应用于环境、药物、食品、生命等许多领域,尤其在吸附重金属、贵金属离子领域有着较为广泛的研究意义。Compared with the traditional liquid-liquid extraction technique, the solid phase extraction method has the following advantages: (1) the operation steps are simple, the analysis speed is fast, and the pretreatment time is shortened; (2) the organic solvent consumption is small, which reduces the experimental cost , while reducing environmental pollution. As a new type of sample pretreatment technology, solid phase extraction has become the most commonly used separation and enrichment method. Therefore, it has developed rapidly in recent years and is widely used in many fields such as environment, medicine, food, life, etc., especially It has extensive research significance in the field of adsorption of heavy metals and noble metal ions.
生物冶金法。生物技术已被成功用于从矿石中提取贵金属和铜。与传统的冶金工艺相比,生物吸附过程具有很多优势,如工艺简单、费用低、操作方便、化学和生物固体副产物少,废水毒性小等优点。主要是浸取时间长,对金属含量高的原料效果不明显。Biometallurgy. Biotechnology has been successfully used to extract precious metals and copper from ores. Compared with the traditional metallurgical process, the biosorption process has many advantages, such as simple process, low cost, convenient operation, less chemical and biological solid by-products, and less toxicity of wastewater. The main reason is that the leaching time is long, and the effect on raw materials with high metal content is not obvious.
国内研究成果。用酸性硫脲溶液从矿石中浸溶金银的方法由前苏联学者在1941年提出。国际上对硫脲提金的理论及工艺开展了广泛的研究。1960年以后,某些冶金工作者曾对之进行了许多理论和应用的研究,建立了小试工厂。20世纪80年代,硫脲浸金才引起个别发达国家的重视。近30年来,原苏联、南非等国家对硫脲法提金做了大量的试验研究。我国近年来在硫脲法提金试验研究方面也进行了许多有益的探索,取得较大的进展。在小型试验基础上,先后在峪耳崖、张家口金矿山进行了每天2吨规模的工业试验;龙水金矿处理每天10吨规模的硫脲提金车间曾投入生产。Domestic research results. The method of leaching gold and silver from ore with acidic thiourea solution was proposed by former Soviet scholars in 1941. Extensive research has been carried out internationally on the theory and technology of thiourea gold extraction. After 1960, some metallurgists have conducted many theoretical and applied researches on it, and established small pilot plants. In the 1980s, thiourea gold immersion attracted the attention of individual developed countries. In the past 30 years, the former Soviet Union, South Africa and other countries have done a lot of experimental research on gold extraction by thiourea method. In recent years, our country has also carried out many beneficial explorations in the experimental research of gold extraction by thiourea method, and made great progress. On the basis of small-scale experiments, industrial experiments with a scale of 2 tons per day have been carried out in Yuerya and Zhangjiakou gold mines; the thiourea gold extraction workshop with a scale of 10 tons per day in Longshui Gold Mine has been put into production.
近十年,国内使用硫脲为络合剂、三价铁为催化剂、双氧水为氧化剂(或者硫脲为络合剂、空气为氧化剂)对酸性、碱性硫脲浸金进行了研究。东华大学的研究人员使用硫氰酸盐为络合剂、二氧化锰为氧化剂也取得很好效果,金浸出率达96%~99%。In the past ten years, domestic studies have been carried out on acidic and alkaline thiourea gold leaching using thiourea as a complexing agent, ferric iron as a catalyst, and hydrogen peroxide as an oxidant (or thiourea as a complexing agent and air as an oxidant). Researchers at Donghua University have also achieved good results using thiocyanate as a complexing agent and manganese dioxide as an oxidant, with a gold leaching rate of 96% to 99%.
然而,如何套用处理液是废电器处理工艺的难题。如果发明一种材料能够吸附处理液中贵金属,处理液可重复使用,将极大节约成本,减少废水排放,产生经济和环保效益。本发明提供一种高效贵金属吸附材料,以硫脲浸出液为废电路板处理液,研究多孔材料的功能。However, how to apply the treatment liquid is a difficult problem in the treatment process of waste electrical appliances. If a material is invented that can absorb precious metals in the treatment solution, the treatment solution can be reused, which will greatly save costs, reduce waste water discharge, and generate economic and environmental benefits. The invention provides a high-efficiency precious metal adsorption material, uses thiourea leaching solution as waste circuit board treatment solution, and studies the function of the porous material.
总之,合成高效的多孔材料,吸附贵金属离子,重复使用废金属处理液,资源化电子废弃物的贵金属和塑料,保护环境,产生经济和社会效益。In short, the synthesis of highly efficient porous materials, the adsorption of noble metal ions, the reuse of waste metal treatment fluids, the recycling of precious metals and plastics from electronic waste, environmental protection, and economic and social benefits.
发明内容Contents of the invention
发明的目的是使用方便的方法合成一种富氮多孔材料MOPs-1,用其吸附贵金属离子,简化工艺流程,多次使用废金属处理液,降低贵金属回收成本,实现变废为宝、减少污染排放的目标,符合环保和绿色环境要求,可以预期该材料会在今后的工业化生产中得到大规模的应用。The purpose of the invention is to use a convenient method to synthesize a nitrogen-rich porous material MOPs-1, use it to absorb precious metal ions, simplify the process flow, use waste metal treatment liquid many times, reduce the cost of precious metal recovery, and realize turning waste into treasure and reducing pollution The discharge target meets the requirements of environmental protection and green environment, and it can be expected that this material will be widely used in industrial production in the future.
为实现上述发明目的,本发明提供的技术方案是:For realizing above-mentioned purpose of the invention, the technical scheme that the present invention provides is:
一种富氮多孔材料,其制备方法步骤为:以乙二醇为溶剂,加入三聚氰胺和对苯醌,加热缩聚,最后加入二甲苯脱水,得到多孔材料MOPs-1。A nitrogen-rich porous material, the preparation method of which comprises the following steps: using ethylene glycol as a solvent, adding melamine and p-benzoquinone, heating and polycondensing, and finally adding xylene for dehydration to obtain the porous material MOPs-1.
进一步的,三聚氰胺与对苯醌的摩尔比为3:(1.9~2.2);摩尔比小于3:1.9或大于3:2.2时,产率明显降低,而且材料物理性能降低。Further, the molar ratio of melamine to p-benzoquinone is 3:(1.9-2.2); when the molar ratio is less than 3:1.9 or greater than 3:2.2, the yield is obviously reduced, and the physical properties of the material are also reduced.
进一步的,加热缩聚时间为5~8小时,时间小于5小时,反应产率降低,产率大于8小时,产率没有明显提高。Further, the heating polycondensation time is 5-8 hours, and if the time is less than 5 hours, the reaction yield will decrease, and if the yield is more than 8 hours, the yield will not be significantly increased.
进一步的,加热温度为160~198℃,温度低于160℃时,反应时间变长,乙二醇沸点为198℃;最后加入二甲苯脱水3~5小时,时间小于3小时缩聚不完全,产率低,大于5小时,没有明显提高。Further, the heating temperature is 160-198°C. When the temperature is lower than 160°C, the reaction time becomes longer, and the boiling point of ethylene glycol is 198°C; finally, xylene is added for dehydration for 3-5 hours. If the time is less than 3 hours, the polycondensation is incomplete, resulting in The rate is low, greater than 5 hours, no significant improvement.
进一步的,脱水温度为二甲苯沸点136~140℃。Further, the dehydration temperature is 136-140°C, the boiling point of xylene.
本发明还公布上述的富氮多孔材料在电路板贵金属回收中的应用。The present invention also discloses the application of the above-mentioned nitrogen-rich porous material in the recovery of circuit board precious metals.
优选的,吸附材料与贵金属质量比例为12~(20:1)。Preferably, the mass ratio of the adsorption material to the noble metal is 12-(20:1).
通过吸附柱试验得到该优选比例:将多孔材料装入吸附柱,将含有贵金属的溶液加入吸附柱,吸附柱吸附贵金属离子。将1%稀盐酸水溶液洗涤吸附柱,贵金属解析。The optimal ratio is obtained through an adsorption column test: the porous material is loaded into the adsorption column, the solution containing the noble metal is added to the adsorption column, and the adsorption column adsorbs the noble metal ions. Wash the adsorption column with 1% dilute hydrochloric acid aqueous solution, and analyze the precious metal.
当实验比例小于12:1时,吸附不完全;比例大于20:1时,剩余贵金属浓度没有明显降低。使用原子吸收光谱判定解吸终点。When the experimental ratio is less than 12:1, the adsorption is not complete; when the ratio is greater than 20:1, the remaining precious metal concentration does not decrease significantly. Desorption endpoints were determined using atomic absorption spectroscopy.
有益效果:Beneficial effect:
废电子器件中贵金属的回收可以减少污染、提供宝贵原材料,保护环境。目前回收贵金属的技术主要有:火法冶金技术、湿法冶金技术、生物冶金技术。湿法冶金技术由于回收金属和塑料具有很好应用前景,但是使用有机溶剂或化学腐蚀性强的王水带来环境污染。近十年,国内使用硫脲或硫氰酸盐为络合剂,取得巨大进展,但是如何节约硫脲或硫氰酸铵溶液,减少污水排放,是该方法能否工业化的关键问题。如果发明一种材料能够吸附处理液中贵金属,处理液可重复使用,将极大节约成本,减少废水排放,产生经济和环保效益。The recovery of precious metals from waste electronic devices can reduce pollution, provide valuable raw materials, and protect the environment. At present, the technologies for recycling precious metals mainly include: pyrometallurgy technology, hydrometallurgy technology, and biometallurgy technology. Hydrometallurgy technology has good application prospects due to the recovery of metals and plastics, but the use of organic solvents or chemically corrosive aqua regia brings environmental pollution. In the past ten years, the use of thiourea or thiocyanate as a complexing agent in China has made great progress, but how to save thiourea or ammonium thiocyanate solution and reduce sewage discharge is the key issue for the industrialization of this method. If a material is invented that can absorb precious metals in the treatment solution, the treatment solution can be reused, which will greatly save costs, reduce waste water discharge, and generate economic and environmental benefits.
本发明提供一种高效贵金属吸附材料MOPs-1,以硫脲浸出液为废电路板处理液,研究多孔材料的功能,能够高效吸附硫脲溶液中贵金属,使硫脲溶液重复使用,从而达到电子废弃物的资源化,回收电子废弃物中的贵金属,并再生塑料,保护环境,产生经济和社会效益。The invention provides a high-efficiency precious metal adsorption material MOPs-1, which uses thiourea leaching solution as waste circuit board treatment liquid to study the function of porous materials, and can efficiently adsorb precious metals in thiourea solution, so that thiourea solution can be reused, so as to achieve electronic waste Recycling of materials, recycling precious metals in electronic waste, and recycling plastics, protecting the environment, and generating economic and social benefits.
附图说明Description of drawings
图1:本发明涉及的材料MOPs-1制备路线及吸附贵金属示意图。Figure 1: A schematic diagram of the preparation route and adsorption of precious metals of the material MOPs-1 involved in the present invention.
图2:MOPs-1、对苯醌(A)和三聚氰胺(B)的红外谱图。Figure 2: Infrared spectra of MOPs-1, p-benzoquinone (A) and melamine (B).
具体实施方式detailed description
下面结合具体实施例对本发明作进一步说明。The present invention will be further described below in conjunction with specific examples.
一种高效贵金属吸附材料MOPs-1,以硫脲浸出液为废电路板处理液,回收电子废弃物中的贵金属。废电子线路板中金属和非金属组分测定如下表1所示:A high-efficiency precious metal adsorption material MOPs-1 uses thiourea leaching solution as waste circuit board treatment liquid to recover precious metals in electronic waste. The determination of metal and non-metal components in waste electronic circuit boards is shown in Table 1 below:
表1Table 1
本发明的材料的合成(实施例1~9)及材料的性质实验(实施例10~12)见以下实施例:材料的合成:The synthesis (embodiment 1~9) of material of the present invention and the property experiment (embodiment 10~12) of material see following embodiment: the synthesis of material:
实施例1Example 1
在1L乙二醇中,加入0.20mol的三聚氰胺和0.30mol的对苯醌,加热,搅拌,保持温度稳定在180℃反应5小时,加入300mL二甲苯,装上分水器,136-140℃二甲苯回流带走水分,缩聚4小时,停止搅拌,自然降温到室温,过滤得棕色沉淀,100mL乙醇洗涤三次,80℃真空干燥,得到棕色块状固体40.5g产率86.5%。In 1L of ethylene glycol, add 0.20mol of melamine and 0.30mol of p-benzoquinone, heat, stir, keep the temperature stable at 180°C for 5 hours, add 300mL of xylene, install a water separator, and set the temperature at 136-140°C for 5 hours The toluene was refluxed to take away the water, polycondensed for 4 hours, stopped stirring, naturally cooled to room temperature, filtered to obtain a brown precipitate, washed three times with 100 mL of ethanol, and dried in vacuum at 80°C to obtain 40.5 g of a brown blocky solid with a yield of 86.5%.
实施例2Example 2
在1L乙二醇中,加入0.19mol的三聚氰胺和0.30mol的对苯醌,加热,搅拌,保持温度稳定在180℃反应5小时,加入300mL二甲苯,装上分水器,136-140℃二甲苯回流带走水分,缩聚4小时,停止搅拌,自然降温到室温,过滤得棕色沉淀,100mL乙醇洗涤三次,80℃真空干燥,得到棕色固体35.6g产率80.1%。In 1L of ethylene glycol, add 0.19mol of melamine and 0.30mol of p-benzoquinone, heat and stir, keep the temperature stable at 180°C for 5 hours, add 300mL of xylene, install a water separator, and set the temperature at 136-140°C Toluene was refluxed to take away water, polycondensed for 4 hours, stopped stirring, naturally cooled to room temperature, filtered to obtain a brown precipitate, washed three times with 100 mL of ethanol, and dried under vacuum at 80°C to obtain 35.6 g of a brown solid with a yield of 80.1%.
实施例3Example 3
在1L乙二醇中,加入0.22mol的三聚氰胺和0.30mol的对苯醌,加热,搅拌,保持温度稳定在180℃反应5小时,加入300mL二甲苯,装上分水器,136-140℃二甲苯回流带走水分,缩聚4小时,停止搅拌,自然降温到室温,过滤得棕色沉淀,100mL乙醇洗涤三次,80℃真空干燥,得到棕色固体40.2g产率85.9%。In 1L of ethylene glycol, add 0.22mol of melamine and 0.30mol of p-benzoquinone, heat, stir, keep the temperature stable at 180°C for 5 hours, add 300mL of xylene, install a water separator, and set the temperature at 136-140°C Toluene was refluxed to take away water, polycondensed for 4 hours, stopped stirring, naturally cooled to room temperature, filtered to obtain a brown precipitate, washed three times with 100 mL of ethanol, and dried in vacuum at 80°C to obtain 40.2 g of a brown solid with a yield of 85.9%.
从实施例1-3可知,当三聚氰胺与对苯醌的摩尔比为1.9~2.2:3时,反应产率较高。将按照三聚氰胺与对苯醌的摩尔比为2:3,在实施例中进一步阐述。It can be seen from Examples 1-3 that when the molar ratio of melamine to p-benzoquinone is 1.9-2.2:3, the reaction yield is higher. According to the molar ratio of melamine and p-benzoquinone being 2:3, it will be further elaborated in the examples.
实施例4Example 4
在1L乙二醇中,加入0.20mol的三聚氰胺和0.30mol的对苯醌,加热,搅拌,保持温度稳定在160℃反应5小时,加入300mL二甲苯,装上分水器,136-140℃二甲苯回流带走水分,缩聚4小时,停止搅拌,自然降温到室温,过滤得棕色沉淀,100mL乙醇洗涤三次,80℃真空干燥,得到棕色固体40.3g产率86.1%。In 1L of ethylene glycol, add 0.20mol of melamine and 0.30mol of p-benzoquinone, heat, stir, keep the temperature stable at 160°C for 5 hours, add 300mL of xylene, install a water separator, and set the temperature at 136-140°C Toluene was refluxed to take away water, polycondensed for 4 hours, stopped stirring, naturally cooled to room temperature, filtered to obtain a brown precipitate, washed three times with 100 mL of ethanol, and dried in vacuum at 80°C to obtain 40.3 g of a brown solid with a yield of 86.1%.
实施例5Example 5
在1L乙二醇中,加入0.20mol的三聚氰胺和0.30mol的对苯醌,加热,搅拌,保持温度稳定在198℃反应5小时,加入300mL二甲苯,装上分水器,136-140℃二甲苯回流带走水分,缩聚4小时,停止搅拌,自然降温到室温,过滤得棕色沉淀,100mL乙醇洗涤三次,80℃真空干燥,得到棕色固体40.5g产率86.5%。In 1L of ethylene glycol, add 0.20mol of melamine and 0.30mol of p-benzoquinone, heat, stir, keep the temperature stable at 198°C for 5 hours, add 300mL of xylene, install a water separator, and set the temperature at 136-140°C Toluene was refluxed to take away water, polycondensed for 4 hours, stopped stirring, naturally cooled to room temperature, filtered to obtain a brown precipitate, washed three times with 100 mL of ethanol, and dried under vacuum at 80°C to obtain 40.5 g of a brown solid with a yield of 86.5%.
从实施例1、4、5可知,当反应温度在160~198℃时,反应产率稳定。将按照180℃在实施例中进一步阐述。It can be known from Examples 1, 4, and 5 that when the reaction temperature is 160-198° C., the reaction yield is stable. It will be further illustrated in the examples according to 180°C.
实施例6Example 6
在1L乙二醇中,加入0.20mol的三聚氰胺和0.30mol的对苯醌,加热,搅拌,保持温度稳定在180℃反应8小时,加入300mL二甲苯,装上分水器,136-140℃二甲苯回流带走水分,缩聚4小时,停止搅拌,自然降温到室温,过滤得棕色沉淀,100mL乙醇洗涤三次,80℃真空干燥,得到棕色固体40.3g产率86.1%。In 1L of ethylene glycol, add 0.20mol of melamine and 0.30mol of p-benzoquinone, heat, stir, keep the temperature stable at 180°C for 8 hours, add 300mL of xylene, install a water separator, and set the temperature at 136-140°C The toluene was refluxed to take away the moisture, polycondensed for 4 hours, stopped stirring, naturally cooled to room temperature, filtered to obtain a brown precipitate, washed three times with 100 mL of ethanol, and dried under vacuum at 80°C to obtain 40.3 g of a brown solid with a yield of 86.1%.
实施例7Example 7
在1L乙二醇中,加入0.20mol的三聚氰胺和0.30mol的对苯醌,加热,搅拌,保持温度稳定在180℃反应6.5小时,加入300mL二甲苯,装上分水器,136-140℃二甲苯回流带走水分,缩聚4小时,停止搅拌,自然降温到室温,过滤得棕色沉淀,100mL乙醇洗涤三次,80℃真空干燥,得到棕色固体40.5g产率86.5%。In 1L of ethylene glycol, add 0.20mol of melamine and 0.30mol of p-benzoquinone, heat and stir, keep the temperature stable at 180°C for 6.5 hours, add 300mL of xylene, install a water separator, and set the temperature at 136-140°C for 6.5 hours Toluene was refluxed to take away water, polycondensed for 4 hours, stopped stirring, naturally cooled to room temperature, filtered to obtain a brown precipitate, washed three times with 100 mL of ethanol, and dried under vacuum at 80°C to obtain 40.5 g of a brown solid with a yield of 86.5%.
从实施例1、6、7可知,当反应时间在5-8小时,反应产率稳定。将按照5小时在实施例中进一步阐述。As can be seen from Examples 1, 6, and 7, when the reaction time was 5-8 hours, the reaction yield was stable. This will be further illustrated in the Examples in terms of 5 hours.
实施例8Example 8
在1L乙二醇中,加入0.20mol的三聚氰胺和0.30mol的对苯醌,加热,搅拌,保持温度稳定在180℃反应5小时,加入300mL二甲苯,装上分水器,136-140℃二甲苯回流带走水分,缩聚3小时,停止搅拌,自然降温到室温,过滤得棕色沉淀,100mL乙醇洗涤三次,80℃真空干燥,得到棕色固体40.2g产率85.9%。In 1L of ethylene glycol, add 0.20mol of melamine and 0.30mol of p-benzoquinone, heat, stir, keep the temperature stable at 180°C for 5 hours, add 300mL of xylene, install a water separator, and set the temperature at 136-140°C for 5 hours Toluene was refluxed to take away water, polycondensed for 3 hours, stopped stirring, naturally cooled to room temperature, filtered to obtain a brown precipitate, washed three times with 100 mL of ethanol, and dried in vacuum at 80°C to obtain 40.2 g of a brown solid with a yield of 85.9%.
实施例9Example 9
在1L乙二醇中,加入0.20mol的三聚氰胺和0.30mol的对苯醌,加热,搅拌,保持温度稳定在180℃反应5小时,加入300mL二甲苯,装上分水器,136-140℃二甲苯回流带走水分,缩聚5小时,停止搅拌,自然降温到室温,过滤得棕色沉淀,100mL乙醇洗涤三次,80℃真空干燥,得到棕色固体40.1g产率85.7%。In 1L of ethylene glycol, add 0.20mol of melamine and 0.30mol of p-benzoquinone, heat, stir, keep the temperature stable at 180°C for 5 hours, add 300mL of xylene, install a water separator, and set the temperature at 136-140°C Toluene was refluxed to take away water, polycondensed for 5 hours, stopped stirring, naturally cooled to room temperature, filtered to obtain a brown precipitate, washed three times with 100 mL of ethanol, and dried under vacuum at 80°C to obtain 40.1 g of a brown solid with a yield of 85.7%.
材料的性质实验:Experiments on the properties of materials:
实施例10Example 10
取上述多孔材料2g,加入含有3L含有金离子0.051wt%,硫脲20wt%,pH=2.5的水溶液中,室温搅拌30min,过滤,原子吸收光谱测定剩余金离子浓度为16ppm,吸附率96.8%。Take 2 g of the above-mentioned porous material, add it to 3 L of aqueous solution containing 0.051 wt % of gold ions, 20 wt % of thiourea, and pH=2.5, stir at room temperature for 30 min, filter, and the remaining gold ion concentration is 16 ppm as determined by atomic absorption spectrometry, and the adsorption rate is 96.8%.
将吸附金的材料装入吸附柱,使用1%的盐酸溶液洗脱,原子吸收光谱测定流出盐酸溶液中金离子浓度小于3ppm时停止洗脱,用去盐酸25mL。The gold-absorbing material is loaded into an adsorption column, and eluted with 1% hydrochloric acid solution. When the gold ion concentration in the effluent hydrochloric acid solution is determined by atomic absorption spectroscopy, the elution is stopped when it is less than 3 ppm, and 25 mL of hydrochloric acid is removed.
实施例11Example 11
取上述多孔材料2g,加入含有300mL含有银离子0.89wt%,硫脲20wt%,pH=2.5的水溶液中,室温搅拌30min,过滤,原子吸收光谱测定剩余银离子浓度为156ppm,吸附率98.2%。Take 2 g of the above-mentioned porous material, add it into 300 mL of an aqueous solution containing 0.89 wt % of silver ions, 20 wt % of thiourea, and pH=2.5, stir at room temperature for 30 min, filter, and the concentration of remaining silver ions determined by atomic absorption spectroscopy is 156 ppm, and the adsorption rate is 98.2%.
将吸附银的材料装入吸附柱,使用1%的硝酸溶液洗脱,原子吸收光谱测定流出硝酸溶液中银离子浓度小于3ppm时停止洗脱,用去硝酸20mL。The silver-absorbing material is packed into an adsorption column, and eluted with 1% nitric acid solution. When the concentration of silver ions in the effluent nitric acid solution is measured by atomic absorption spectrometry, the elution is stopped when the concentration of silver ions is less than 3 ppm, and 20 mL of nitric acid is removed.
实施例12Example 12
取上述多孔材料2g,加入含有300mL含有银离子0.89wt%,金离子215ppm,硫脲20wt%,pH=2.5的水溶液中,室温搅拌30min,过滤,原子吸收光谱测定剩余金、银离子浓度分别为10ppm、152ppm,吸附率分别为95.3%、98.3%。Get above-mentioned porous material 2g, add and contain 300mL and contain silver ion 0.89wt%, gold ion 215ppm, thiourea 20wt%, in the aqueous solution of pH=2.5, stir at room temperature 30min, filter, atomic absorption spectrometry determines remaining gold, silver ion concentration is respectively 10ppm, 152ppm, the adsorption rates are 95.3%, 98.3%, respectively.
将吸附贵金属的材料装入吸附柱,先用20mL 1%的硝酸溶液洗脱,再用10mL 1%的盐酸溶液洗脱,原子吸收光谱测定流出贵金属离子浓度小于3ppm时停止洗脱。Put the material adsorbing precious metals into the adsorption column, first elute with 20mL of 1% nitric acid solution, then with 10mL of 1% hydrochloric acid solution, and stop elution when the concentration of outflowing noble metal ions is less than 3ppm as determined by atomic absorption spectrometry.
以上所述,仅是本发明的较佳实施例,并非对本发明作任何形式上的限制,任何熟悉本专业的技术人员,在不脱离本发明技术方案范围内,依据本发明的技术实质,对以上实施例所作的任何简单的修改、等同替换与改进等,均仍属于本发明技术方案的保护范围之内。The above are only preferred embodiments of the present invention, and are not intended to limit the present invention in any form. Any skilled person who is familiar with the profession, without departing from the scope of the technical solutions of the present invention, according to the technical essence of the present invention, Any simple modifications, equivalent replacements and improvements made in the above embodiments still fall within the protection scope of the technical solution of the present invention.
Claims (8)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201710574514.1A CN107308918A (en) | 2017-07-14 | 2017-07-14 | A kind of preparation method of rich nitride polyporous material and its in retrieving circuit board noble metal application |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201710574514.1A CN107308918A (en) | 2017-07-14 | 2017-07-14 | A kind of preparation method of rich nitride polyporous material and its in retrieving circuit board noble metal application |
Publications (1)
Publication Number | Publication Date |
---|---|
CN107308918A true CN107308918A (en) | 2017-11-03 |
Family
ID=60178463
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201710574514.1A Pending CN107308918A (en) | 2017-07-14 | 2017-07-14 | A kind of preparation method of rich nitride polyporous material and its in retrieving circuit board noble metal application |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN107308918A (en) |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108371946A (en) * | 2018-05-08 | 2018-08-07 | 南京信息工程大学 | A kind of application by bisphenol-A and the preparation method and its absorbing heavy metal ions in water of the rich nitride polyporous material of melamine polycondensation |
CN108421540A (en) * | 2018-05-07 | 2018-08-21 | 南京信息工程大学 | A kind of melamine-based organic porous material and preparation method thereof |
CN108467492A (en) * | 2018-05-07 | 2018-08-31 | 南京信息工程大学 | A kind of fluorine-containing organic metal porous material and preparation method thereof |
CN109499614A (en) * | 2018-12-12 | 2019-03-22 | 怀化学院 | MOPs loads bidentate chelating type metallic catalyst and preparation method thereof |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN104910379A (en) * | 2014-03-12 | 2015-09-16 | 周卫星 | Preparation method of amino group-containing porous material, and application of amino group-containing porous material in recover of waste electric appliance precious metals |
CN106563418A (en) * | 2015-10-09 | 2017-04-19 | 中国科学院大连化学物理研究所 | Preparation of nitrogen-enriched organic porous material, and organic porous material and application thereof |
-
2017
- 2017-07-14 CN CN201710574514.1A patent/CN107308918A/en active Pending
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN104910379A (en) * | 2014-03-12 | 2015-09-16 | 周卫星 | Preparation method of amino group-containing porous material, and application of amino group-containing porous material in recover of waste electric appliance precious metals |
CN106563418A (en) * | 2015-10-09 | 2017-04-19 | 中国科学院大连化学物理研究所 | Preparation of nitrogen-enriched organic porous material, and organic porous material and application thereof |
Non-Patent Citations (1)
Title |
---|
吴虹 等: ""醌胺聚合反应动力学研究"", 《 上海大学学报(自然科学版)》 * |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108421540A (en) * | 2018-05-07 | 2018-08-21 | 南京信息工程大学 | A kind of melamine-based organic porous material and preparation method thereof |
CN108467492A (en) * | 2018-05-07 | 2018-08-31 | 南京信息工程大学 | A kind of fluorine-containing organic metal porous material and preparation method thereof |
CN108371946A (en) * | 2018-05-08 | 2018-08-07 | 南京信息工程大学 | A kind of application by bisphenol-A and the preparation method and its absorbing heavy metal ions in water of the rich nitride polyporous material of melamine polycondensation |
CN109499614A (en) * | 2018-12-12 | 2019-03-22 | 怀化学院 | MOPs loads bidentate chelating type metallic catalyst and preparation method thereof |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
Ashiq et al. | Hydrometallurgical recovery of metals from e-waste | |
CN104630479B (en) | A kind of method reclaiming various metals from electron wastes | |
CN107308918A (en) | A kind of preparation method of rich nitride polyporous material and its in retrieving circuit board noble metal application | |
CN103114202B (en) | Comprehensive recovery process for environment-friendly type refractory gold-silver ore multi-metals | |
CN101139660A (en) | Method for extracting iron-lead and gold-silver from gold concentrate acidifying baking residue | |
CN103695662B (en) | Comprehensive utilization method of slag iron concentrates of wet-type zinc smelting furnace | |
CN102560126A (en) | Method for extracting gold and/or silver from sulfuric acid slag | |
CN102660676A (en) | Method for separating rhenium and molybdenum in molybdenum-rhenium ore concentrate | |
CN104910379B (en) | Preparation method of amino group-containing porous material, and application of amino group-containing porous material in recover of waste electric appliance precious metals | |
CA2865721C (en) | Method of recovering gold adsorbed on activated carbon and method of manufacturing gold using the same | |
Wei et al. | Trash or treasure? Sustainable noble metal recovery | |
CN106319199A (en) | Pretreatment method of antimony-and arsenic-containing refractory gold ore | |
CN114134337A (en) | Low-cost and efficient method for recovering precious metals in circuit board components | |
Regel-Rosocka | Electronic wastes | |
US20230175096A1 (en) | Cost-effective method for recovering precious metals in circuit board components | |
Ji et al. | Current progress on gold recovery from refractory ore and waste electrical and electronic equipment | |
CN110607450A (en) | A method for selective leaching and precipitation recovery of palladium in printed circuit boards | |
CN102925700A (en) | Method for recovering precious metal from electronic waste | |
CN101314823B (en) | Method for extracting thallium from thallium containing slag | |
CN113292498B (en) | 3-peroxybenzoic acid-1-methylimidazole chloride salt and preparation and application thereof | |
CN105907976B (en) | One kind Recover palladium from waste mobile phone electronic component(Pd)Method | |
CN112342384B (en) | Method for recycling waste circuit board and waste oxidizing solution in synergy manner | |
CN103131864B (en) | Method for pre-treating complex indium-containing smoke dust by microwave roasting | |
CN108179278B (en) | A kind of precious metal extraction solution, preparation method and application thereof | |
CN106148704B (en) | One kind recycles gold from waste mobile phone electronic component(Au)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 | ||
CB02 | Change of applicant information | ||
CB02 | Change of applicant information |
Address after: 210044 Ning six road, Pukou District, Nanjing, Jiangsu Province, No. 219 Applicant after: Nanjing University of Information Science and Technology Address before: No. 69, Jianye District, Jianye District, Nanjing, Jiangsu Applicant before: Nanjing University of Information Science and Technology |
|
RJ01 | Rejection of invention patent application after publication | ||
RJ01 | Rejection of invention patent application after publication |
Application publication date: 20171103 |