非金属矿
非金屬礦
비금속광
Non-Metallic Mines
2015年
5期
71-73,77
,共4页
肖利萍%栾雪菲%白际驰%郭悦
肖利萍%欒雪菲%白際馳%郭悅
초리평%란설비%백제치%곽열
膨润土%钢渣%Cu2+%吸附
膨潤土%鋼渣%Cu2+%吸附
팽윤토%강사%Cu2+%흡부
bentonite%steel slag%Cu2+%adsorption
采用碱性及吸附性强的环境矿物材料膨润土、钢渣及其混合物对含Cu2+酸性矿山废水进行对比处理试验研究,结果表明:膨润土、钢渣混合后比单一膨润土和单一钢渣的处理效果更好,膨润土、钢渣混合后可发生吸附-聚沉协同作用,更有利于Cu2+的去除。对于pH值为3.5~4, Cu2+质量浓度为50 mg/L的含Cu2+酸性矿山废水,当膨润土、钢渣质量混合比分别为5∶5和8∶2时,在投加量为2 g/L时,去除效果较好。吸附反应120 min时,可使废水pH值分别达到8.67和7.21,Cu2+去除率分别为95.80%和93.94%;膨润土、钢渣复合吸附剂对铜离子的吸附过程符合伪二级动力学方程,相关系数均可达到0.998以上,其吸附过程以化学吸附为主,并伴有液膜扩散及颗粒内扩散。膨润土、钢渣混合材料可作为处理含Cu2+酸性矿山废水的优良吸附材料,5∶5膨润土-钢渣复合吸附材料效果更好。
採用堿性及吸附性彊的環境礦物材料膨潤土、鋼渣及其混閤物對含Cu2+痠性礦山廢水進行對比處理試驗研究,結果錶明:膨潤土、鋼渣混閤後比單一膨潤土和單一鋼渣的處理效果更好,膨潤土、鋼渣混閤後可髮生吸附-聚沉協同作用,更有利于Cu2+的去除。對于pH值為3.5~4, Cu2+質量濃度為50 mg/L的含Cu2+痠性礦山廢水,噹膨潤土、鋼渣質量混閤比分彆為5∶5和8∶2時,在投加量為2 g/L時,去除效果較好。吸附反應120 min時,可使廢水pH值分彆達到8.67和7.21,Cu2+去除率分彆為95.80%和93.94%;膨潤土、鋼渣複閤吸附劑對銅離子的吸附過程符閤偽二級動力學方程,相關繫數均可達到0.998以上,其吸附過程以化學吸附為主,併伴有液膜擴散及顆粒內擴散。膨潤土、鋼渣混閤材料可作為處理含Cu2+痠性礦山廢水的優良吸附材料,5∶5膨潤土-鋼渣複閤吸附材料效果更好。
채용감성급흡부성강적배경광물재료팽윤토、강사급기혼합물대함Cu2+산성광산폐수진행대비처리시험연구,결과표명:팽윤토、강사혼합후비단일팽윤토화단일강사적처리효과경호,팽윤토、강사혼합후가발생흡부-취침협동작용,경유리우Cu2+적거제。대우pH치위3.5~4, Cu2+질량농도위50 mg/L적함Cu2+산성광산폐수,당팽윤토、강사질량혼합비분별위5∶5화8∶2시,재투가량위2 g/L시,거제효과교호。흡부반응120 min시,가사폐수pH치분별체도8.67화7.21,Cu2+거제솔분별위95.80%화93.94%;팽윤토、강사복합흡부제대동리자적흡부과정부합위이급동역학방정,상관계수균가체도0.998이상,기흡부과정이화학흡부위주,병반유액막확산급과립내확산。팽윤토、강사혼합재료가작위처리함Cu2+산성광산폐수적우량흡부재료,5∶5팽윤토-강사복합흡부재료효과경호。
Basic and high adsorbability materials such as bentonite, steel slag and the mixture of two materials are prepared to treat acid mine drainage containing Cu2+. The results showed that the mixture of two materials had a better effect than the single bentonite and the single steel slag. When the two absorbent materials were mixed to treat acid mine drainage containing Cu2+, the mixture could treat Cu2+ better with the adsorption-coagulation synergy. Under treatment conditions of the mixing ratios of bentonite, steel slag were 5∶5 and 8∶2, mixture usage of 2 g/L, initial pH value 3.5~4, the removal efifciency of Cu2+ was excellent at 50 mg/L initial concentration.when adsorption reacts 120 min, the wastewater pH value were 8.67 and 7.21, respectively; the removal rates of Cu2+ were 95.80% and 93.94%, respectively. The coefifcient of determination (R2>0.998) agreed well with pseudo second-order kinetics. The main adsorption process is chemical adsorption. Liquid iflm diffusion and intra-particle diffusion are secondary. The mixture of bentonite and steel slag as a excellent absorbent material can treat acid mine drainage containing Cu2+, especially the material mixing ratio of 5∶5.