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利用尾矿固体废弃物制备吸附材料处理废水重金属污染是重要的技术手段,然而目前针对铅锌尾矿基吸附材料的系统性研究较为匮乏。通过热活化某铅锌尾矿(LZT)后复合海藻酸钠(SA)制备新型吸附材料并用于重金属Cu2+和Cd2+的处理。在850℃下短时热活化的铅锌尾矿(LZT850)结晶度提升,碳酸盐分解后形成的孔隙结构紧密相连,具有较高的比表面积(5.463 3 m2/g)。利用4g/LSA与LZT850在20℃下复合90 min后,得到的LZT850@SA呈现出复杂交联网络结构,具有最大比表面积(16.3109m2/g),孔容量为0.111508cm3/g。LZT850@SA在pH=6时对Cu2+和Cd2+的饱和吸附量分别为223.15和228.05 mg/g,均在120min达到吸附平衡,适量升温有助于吸附性能提升。该方法为铅锌尾矿基重金属吸附材料的制备提供了新的思路和参考。
Abstract:Lead-zinc ore is an important part of non-ferrous mineral resources in the world. In the mining and flotation process of lead-zinc ore, a large amount of lead-zinc tailings(LZT) will be produced, which not only occupies scarce land resources, but also seriously pollutes the ecological environment around the mine. Therefore,the recycling and utilization of lead-zinc tailings based on resources has great potential and benefits. The leadzinc tailings were thermally modified at different temperatures to prepare adsorption materials. It is ultimately found that the lead-zinc tailings(LZT850) subjected to short-term high-temperature modification at 850 ℃ has a relatively high specific surface area of 5.463 3 m2/g. Lead-zinc tailings-based adsorption materials are similar to other types of tailings-based adsorption materials in practical applications. They still face two key challenges:insufficient structural stability and limited adsorption performance for heavy metal ions. Currently, tailingsbased materials are often modified by methods such as surface functionalization modification, polymer network construction, nanomaterial composite, and pore structure regulation to enhance the adsorption capacity, selectivity,and environmental stability of heavy metal ions. Natural high-molecular compounds have attracted extensive attention in the field of adsorbent modification due to their unique structures and functions. Sodium alginate(SA)is a natural polysaccharide extracted from brown algae. Its molecular chain is rich in carboxyl groups(— COOH)and hydroxyl groups(— OH) functional groups. These functional groups can form complexes with heavy metal ions, thereby significantly enhancing the adsorption performance. Moreover, SA has excellent biocompatibility,degradability and film-forming properties, making it an ideal modified material. To further enhance the adsorption performance, the natural polymer material SA was used to composite-modify LZT850(LZT850@SA). After exploring the composite conditions, it is finally determined that 4 g/L SA solution is used to prepare LZT850@SA adsorption material by magnetic stirring with LZT850 at 20 ℃ for 90 min. The leaching toxicity of LZT850@SA is far below the limit, making it reliable and harmless for application. The specific surface area of LZT850@SA increases from 5.463 3 m2/g to 16.310 9 m2/g compared to LZT850, and the pore volume increases from 0.038 162 cm3/g to 0.111 508 cm3/g. Based on the characteristic results of SEM and TEM, it can be seen that LZT850@SA generates some fibrous and long strip-like structures. The HRTEM image indicates that the amorphous layered structure of SA is closely combined with the crystal plane of LZT850, greatly expanding the specific surface area and porosity of the material. LZT850@SA has a wider applicable pH range. Its adsorption performance remains above 95% in a weakly acidic environment with pH value from 4 to 6. The saturated adsorption capacity for Cu2+ and Cd2+ is 224.37 mg/g and 230.06 mg/g respectively, and the adsorption equilibrium time is about 120 min. Appropriate temperature increase is beneficial to enhance the adsorption performance of LZT850@SA. The research results provide scientific basis and technical support for enhancing the adsorption performance of lead-zinc tailings-based adsorption materials for heavy metal wastewater, and also offer reference for the recycling and utilization of other tailings that has not been studied before.
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基本信息:
DOI:10.20237/j.issn.1007-7545.2025.10.023
中图分类号:X705;TQ424
引用信息:
[1]周鑫煜,孟奇,董鹏.新型铅锌尾矿基复合吸附材料的制备及性能研究[J].有色金属(冶炼部分),2025(10):245-255.DOI:10.20237/j.issn.1007-7545.2025.10.023.
基金信息:
云南省科技重大专项资助项目(202202AG050003)
2025-03-31
2025
2025-04-11
2025-04-14
2025
1
2025-09-28
2025-09-28