中国环境科学
中國環境科學
중국배경과학
CHINA ENVIRONMENTAL SCIENCE
2014年
4期
942-950
,共9页
刘咏%刘娅%任越琳%汪诗翔%赵仕林
劉詠%劉婭%任越琳%汪詩翔%趙仕林
류영%류아%임월림%왕시상%조사림
腐植酸钠%金属离子%凝胶%吸附%F
腐植痠鈉%金屬離子%凝膠%吸附%F
부식산납%금속리자%응효%흡부%F
humic acid sodium%metal ion%gel%adsorption%fluoride%F
为提高水中F-的吸附去除效率,以腐植酸钠(NaA)为原料,用铝盐和钙盐通过凝胶聚合法对其改性,制备了金属离子改性腐植酸钠吸附剂(标记为 MMNaA).用 SEM 及 XRD 表征吸附剂的结构和形貌,通过静态吸附实验探讨了 MMNaA 对水中 F-的吸附性能并与传统的γ-Al2O3吸附剂进行比较.结果表明,MMNaA对水中F-的等温吸附结果与Langmuir方程能较好地拟合,用Langmuir方程计算出的饱和吸附容量为208.77mg/g;吸附过程遵循准2级动力学方程,其速率控制步骤包括边界层扩散和内部扩散2个过程;在pH 5~9时MMNaA对水中F-具有较高的吸附去除率.当吸附剂用于深度处理实际含氟废水时,与γ-Al2O3相比,MMNaA适用的pH值范围更广,满足达标排放时所需的投加量更小、吸附时间更短.
為提高水中F-的吸附去除效率,以腐植痠鈉(NaA)為原料,用鋁鹽和鈣鹽通過凝膠聚閤法對其改性,製備瞭金屬離子改性腐植痠鈉吸附劑(標記為 MMNaA).用 SEM 及 XRD 錶徵吸附劑的結構和形貌,通過靜態吸附實驗探討瞭 MMNaA 對水中 F-的吸附性能併與傳統的γ-Al2O3吸附劑進行比較.結果錶明,MMNaA對水中F-的等溫吸附結果與Langmuir方程能較好地擬閤,用Langmuir方程計算齣的飽和吸附容量為208.77mg/g;吸附過程遵循準2級動力學方程,其速率控製步驟包括邊界層擴散和內部擴散2箇過程;在pH 5~9時MMNaA對水中F-具有較高的吸附去除率.噹吸附劑用于深度處理實際含氟廢水時,與γ-Al2O3相比,MMNaA適用的pH值範圍更廣,滿足達標排放時所需的投加量更小、吸附時間更短.
위제고수중F-적흡부거제효솔,이부식산납(NaA)위원료,용려염화개염통과응효취합법대기개성,제비료금속리자개성부식산납흡부제(표기위 MMNaA).용 SEM 급 XRD 표정흡부제적결구화형모,통과정태흡부실험탐토료 MMNaA 대수중 F-적흡부성능병여전통적γ-Al2O3흡부제진행비교.결과표명,MMNaA대수중F-적등온흡부결과여Langmuir방정능교호지의합,용Langmuir방정계산출적포화흡부용량위208.77mg/g;흡부과정준순준2급동역학방정,기속솔공제보취포괄변계층확산화내부확산2개과정;재pH 5~9시MMNaA대수중F-구유교고적흡부거제솔.당흡부제용우심도처리실제함불폐수시,여γ-Al2O3상비,MMNaA괄용적pH치범위경엄,만족체표배방시소수적투가량경소、흡부시간경단.
Metal ion-modified humic acid sodium absorbent (devoted as MMNaA) had been developed to improve the removal efficiency of fluoride ion in aqueous solution by gel polymerization method using aluminum salt and calcium salt as raw materials. The crystal structures and microstructures of the materials were measured by XRD and SEM; and the adsorption performance of the materials for fluoride ion in aqueous solution was investigated by static adsorption experiment. The results showed that a good matching between the adsorption isotherm behavior of MMNaA and Langmuir equation was observed; the adsorption capacity of 208.77mg/g calculated from Langmuir equation was obtained; the adsorption process could be expressed as pseudo-second-order kinetic model; and the absorption rate was determined by the liquid film diffusion and the intra-particle diffusion. Maximum fluoride adsorption of MMNaA in contaminated water was reached at the pH values of 5~9.As compared with γ-Al2O3, MMNaA had a much wider range of pH, less dose and shorter absorption time.