中华地方病学杂志
中華地方病學雜誌
중화지방병학잡지
Chinese Journal of Endemiology
2014年
1期
41-45
,共5页
陈涛%孙成勋%李文宇%李润琴%李鑫
陳濤%孫成勛%李文宇%李潤琴%李鑫
진도%손성훈%리문우%리윤금%리흠
骨炭%改性黏土%饮用水%降氟
骨炭%改性黏土%飲用水%降氟
골탄%개성점토%음용수%강불
Bone char%Modified clay%Drinking%Defluorination
目的 对比两种除氟剂(骨炭、改性黏土)的除氟效果,分析两种除氟剂在小城镇地区饮水除氟应用的可行性.方法 对骨炭、改性黏土两种除氟剂在相同条件下进行除氟效果影响因素研究,观察吸附时间、温度、pH值、阴阳离子、固液比对除氟效果的影响.采用地下水源水对两种除氟剂的除氟效果进行验证.对骨炭和改性黏土除氟剂分别采用氢氧化钠(NaOH)和硫酸铝[Al2(SO4)3]进行再生实验,观察再生效果.结果 两种除氟剂对氟的吸附过程符合Langmuir吸附等温线,对氟理论最大吸附容量分别为10.225 g/kg(骨炭)和0.587g/kg(改性黏土).温度对两种除氟剂除氟效果影响不大,随温度的升高(10~ 35℃),骨炭对氟的吸附容量变化范围为1.568~ 1.598g/kg,改性黏土对氟的吸附容量变化范围为0.423~0.470g/kg.低pH条件下有利于两种除氟剂对氟的去除,随着pH值的升高(4~ 10),骨炭对氟的吸附容量由1.598g/kg下降至1.523g/kg,改性黏土对氟的吸附容量由0.724g/kg下降至0.320 g/kg.地下水中常见阳离子钙(Ca2+)对除氟效果起到一定的促进作用,随含量增加,骨炭对氟的吸附容量可升高至1.713 g/kg,改性黏土对氟的吸附容量可升高至0.485g/kg;阴离子碳酸氢根(HCO3-)和硫酸根(SO42-)随含量增加对除氟有不同程度的抑制作用,骨炭对氟的吸附容量可最低降至1.158 g/kg(HCO3-),改性黏土对氟的吸附容量可最低降至0.237 g/kg(SO2-).除氟后的骨炭可通过NaOH浸泡的方式再生,改性黏土可通过Al2(SO4)3浸泡的方式再生,3次再生后两种除氟剂的吸附效率仍可达原来的94.6%和97.3%.结论 骨炭除氟剂和改性黏土除氟剂均具有良好的除氟效果并可多次再生使用,简便易行,完全适合在小城镇地区应用.骨炭除氟剂适合家庭式除氟,改性黏土除氟剂适合集中式饮用水除氟.
目的 對比兩種除氟劑(骨炭、改性黏土)的除氟效果,分析兩種除氟劑在小城鎮地區飲水除氟應用的可行性.方法 對骨炭、改性黏土兩種除氟劑在相同條件下進行除氟效果影響因素研究,觀察吸附時間、溫度、pH值、陰暘離子、固液比對除氟效果的影響.採用地下水源水對兩種除氟劑的除氟效果進行驗證.對骨炭和改性黏土除氟劑分彆採用氫氧化鈉(NaOH)和硫痠鋁[Al2(SO4)3]進行再生實驗,觀察再生效果.結果 兩種除氟劑對氟的吸附過程符閤Langmuir吸附等溫線,對氟理論最大吸附容量分彆為10.225 g/kg(骨炭)和0.587g/kg(改性黏土).溫度對兩種除氟劑除氟效果影響不大,隨溫度的升高(10~ 35℃),骨炭對氟的吸附容量變化範圍為1.568~ 1.598g/kg,改性黏土對氟的吸附容量變化範圍為0.423~0.470g/kg.低pH條件下有利于兩種除氟劑對氟的去除,隨著pH值的升高(4~ 10),骨炭對氟的吸附容量由1.598g/kg下降至1.523g/kg,改性黏土對氟的吸附容量由0.724g/kg下降至0.320 g/kg.地下水中常見暘離子鈣(Ca2+)對除氟效果起到一定的促進作用,隨含量增加,骨炭對氟的吸附容量可升高至1.713 g/kg,改性黏土對氟的吸附容量可升高至0.485g/kg;陰離子碳痠氫根(HCO3-)和硫痠根(SO42-)隨含量增加對除氟有不同程度的抑製作用,骨炭對氟的吸附容量可最低降至1.158 g/kg(HCO3-),改性黏土對氟的吸附容量可最低降至0.237 g/kg(SO2-).除氟後的骨炭可通過NaOH浸泡的方式再生,改性黏土可通過Al2(SO4)3浸泡的方式再生,3次再生後兩種除氟劑的吸附效率仍可達原來的94.6%和97.3%.結論 骨炭除氟劑和改性黏土除氟劑均具有良好的除氟效果併可多次再生使用,簡便易行,完全適閤在小城鎮地區應用.骨炭除氟劑適閤傢庭式除氟,改性黏土除氟劑適閤集中式飲用水除氟.
목적 대비량충제불제(골탄、개성점토)적제불효과,분석량충제불제재소성진지구음수제불응용적가행성.방법 대골탄、개성점토량충제불제재상동조건하진행제불효과영향인소연구,관찰흡부시간、온도、pH치、음양리자、고액비대제불효과적영향.채용지하수원수대량충제불제적제불효과진행험증.대골탄화개성점토제불제분별채용경양화납(NaOH)화류산려[Al2(SO4)3]진행재생실험,관찰재생효과.결과 량충제불제대불적흡부과정부합Langmuir흡부등온선,대불이론최대흡부용량분별위10.225 g/kg(골탄)화0.587g/kg(개성점토).온도대량충제불제제불효과영향불대,수온도적승고(10~ 35℃),골탄대불적흡부용량변화범위위1.568~ 1.598g/kg,개성점토대불적흡부용량변화범위위0.423~0.470g/kg.저pH조건하유리우량충제불제대불적거제,수착pH치적승고(4~ 10),골탄대불적흡부용량유1.598g/kg하강지1.523g/kg,개성점토대불적흡부용량유0.724g/kg하강지0.320 g/kg.지하수중상견양리자개(Ca2+)대제불효과기도일정적촉진작용,수함량증가,골탄대불적흡부용량가승고지1.713 g/kg,개성점토대불적흡부용량가승고지0.485g/kg;음리자탄산경근(HCO3-)화류산근(SO42-)수함량증가대제불유불동정도적억제작용,골탄대불적흡부용량가최저강지1.158 g/kg(HCO3-),개성점토대불적흡부용량가최저강지0.237 g/kg(SO2-).제불후적골탄가통과NaOH침포적방식재생,개성점토가통과Al2(SO4)3침포적방식재생,3차재생후량충제불제적흡부효솔잉가체원래적94.6%화97.3%.결론 골탄제불제화개성점토제불제균구유량호적제불효과병가다차재생사용,간편역행,완전괄합재소성진지구응용.골탄제불제괄합가정식제불,개성점토제불제괄합집중식음용수제불.
Objective To compare the effectiveness of two kinds of defluorinating agents (bone char and modified clay) for removal of fluoride in drinking water,and to analyze their application feasibility in small towns.Methods Influencing factors on defluorinating efficiencies of the two kinds of defluorinating agents under the same conditions were studied,namely the effects of adsorption time,temperature,pH,common anions and cations,and solid-liquid ratio on defluorinating efficiencies were studied.The defluorinating efficiencies of the two kinds of defluorinating agents were validated by original groundwater in Jilin Province.The homemade bone char defluorinating agent and modified clay defluorinating agent were regenerated by NaOH and Al2(SO4)3,respectively,and their regeneration abilities were investigated.Results The adsorption data of the two kinds of defluorinating agents were fitted Langmuir model well,and the maximum adsorption capacities were 10.225 g/kg(bone char) and 0.587 g/kg(modified clay).The effect of temperature on defluorinating efficiencies was limited,with increasing temperature(10-35 ℃),the adsorption capacity of bone char and modified clay for fluoride ranged from 1.568 g/kg to 1.598 g/kg and 0.423 g/kg to 0.470 g/kg,respectively.Fluoride could be easily removed under low pH conditions,with increasing of pH(4-10),the adsorption capacity of bone char and modified clay for fluoride decreased from 1.598 g/kg to 1.523 g/kg and 0.724 g/kg to 0.320 g/kg,respectively.The defluorinating efficiencies were improved by common cations(Ca2+) in groundwater,and the adsorption capacity of bone char and modified clay for fluoride increased to 1.713 g/kg and 0.485 g/kg,respectively.Whereas,the defluorinating efficiencies were inhibited by common anions(HCO3-,SO42-) at a certain degree,and the adsorption capacities of bone char and modified clay for fluoride were decreased to 1.158 g/kg(HCO3-) and 0.237 g/kg(SO42),respectively.Defluoridation bone char could be regenerated by soaking in NaOH,and modified clay by immersion in Al2(SO4)3.The adsorption capacities of the two defluorinating agents that had been regenerated for three times still reached 94.6% and 97.3% of their original capacities.Conclusions Both of the homemade bone char defluorinating agent and modified clay defluorinating agent have good defluorinating efficiencies and can be regenerated for many times,which are perfectly suitable for application in small towns since they are simple and can be easily applied.The homemade bone char defluorinating agent is suitable for family drinking water and the homemade modified clay defluorinating agent would be more suitable for centralized drinking water.