Chemical Industry and Engineering Progress ›› 2024, Vol. 43 ›› Issue (4): 1655-1666.DOI: 10.16085/j.issn.1000-6613.2023-0715
• Chemical processes and equipment • Previous Articles
DU Yongliang1,2(), LIANG Zhuobin1,2, GONG Yaoxu1,2, BI Haojie1,2, XU Zhiyuan1,2, YUAN Hongying1,2,3()
Received:
2023-05-04
Revised:
2023-08-29
Online:
2024-05-13
Published:
2024-04-15
Contact:
YUAN Hongying
杜永亮1,2(), 梁卓彬1,2, 龚耀煦1,2, 毕豪杰1,2, 徐志远1,2, 苑宏英1,2,3()
通讯作者:
苑宏英
作者简介:
杜永亮(1985—),男,博士,讲师,研究方向为污水污泥处理、固废资源化处置。E-mail:du.smile@163.com。
基金资助:
CLC Number:
DU Yongliang, LIANG Zhuobin, GONG Yaoxu, BI Haojie, XU Zhiyuan, YUAN Hongying. Air gap membrane distillation research status and applications[J]. Chemical Industry and Engineering Progress, 2024, 43(4): 1655-1666.
杜永亮, 梁卓彬, 龚耀煦, 毕豪杰, 徐志远, 苑宏英. 气隙式膜蒸馏技术研究现状和应用[J]. 化工进展, 2024, 43(4): 1655-1666.
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URL: https://hgjz.cip.com.cn/EN/10.16085/j.issn.1000-6613.2023-0715
基膜 | 强化形式 | 优化结果 | 参考文献 |
---|---|---|---|
PSF(聚砜)膜 | 将吐温80或磺化聚砜(SPSF)加入聚砜-聚乙二醇400-二甲基乙酰胺体系中用浸入沉淀相转化法制备PS中空纤维膜 | SPSF对膜的亲水性改善比吐温80好;SPSF质量分数为1.5%时可将膜通量提升一倍以上,可达302L/(m2·h) | [ |
PP膜 | 用共沉积法让亲水性聚多巴胺/聚乙烯亚胺在PP中空纤维膜管腔内沉积制成Janus膜 | 使用2g/L的聚多巴胺/聚乙烯亚胺共沉积液在60℃下沉积6h约提升85%,70℃下沉积6h约提升100%,80℃下沉积6h可使得通量提升120%,且具有良好的耐盐和抗污染性 | [ |
PVDF膜 | 通过多巴胺的自附着行为对PTFE中空纤维膜进行表面改性 | 用2g/L的多巴胺对PTFE中空纤维膜进行表面改性8h后得到的膜丝的纯水通量为原膜的1.5倍 | [ |
PVDF膜 | 用热致相分离法制备PVDF/SMA共混中空纤维膜 | PVDF/SMA共混膜的膜通量由19.23L/(m2·h)提升到了62.39L/(m2·h),水接触角由93.4°降低到66.9° | [ |
PVDF膜 | 双喷头对喷的静电纺织制备PVDF-PH-PET交织型的多级纤维复合膜(tHFC) | 在温差为40℃、PET/PH为0.8/1.5、膜厚为80μm的条件下,膜通量可达65.86L/(m2·h) | [ |
PVDF膜 | 蚀刻-电喷雾协同技术使用Al2O3纳米颗粒对PVDF膜改性制成有微/纳凹结构的亲/疏水Janus膜 | 相较PVDF膜和双疏膜处理高盐含油废水时30min就被污染,Janus膜可连续稳定运行45h仍未被污染 | [ |
基膜 | 强化形式 | 优化结果 | 参考文献 |
---|---|---|---|
PSF(聚砜)膜 | 将吐温80或磺化聚砜(SPSF)加入聚砜-聚乙二醇400-二甲基乙酰胺体系中用浸入沉淀相转化法制备PS中空纤维膜 | SPSF对膜的亲水性改善比吐温80好;SPSF质量分数为1.5%时可将膜通量提升一倍以上,可达302L/(m2·h) | [ |
PP膜 | 用共沉积法让亲水性聚多巴胺/聚乙烯亚胺在PP中空纤维膜管腔内沉积制成Janus膜 | 使用2g/L的聚多巴胺/聚乙烯亚胺共沉积液在60℃下沉积6h约提升85%,70℃下沉积6h约提升100%,80℃下沉积6h可使得通量提升120%,且具有良好的耐盐和抗污染性 | [ |
PVDF膜 | 通过多巴胺的自附着行为对PTFE中空纤维膜进行表面改性 | 用2g/L的多巴胺对PTFE中空纤维膜进行表面改性8h后得到的膜丝的纯水通量为原膜的1.5倍 | [ |
PVDF膜 | 用热致相分离法制备PVDF/SMA共混中空纤维膜 | PVDF/SMA共混膜的膜通量由19.23L/(m2·h)提升到了62.39L/(m2·h),水接触角由93.4°降低到66.9° | [ |
PVDF膜 | 双喷头对喷的静电纺织制备PVDF-PH-PET交织型的多级纤维复合膜(tHFC) | 在温差为40℃、PET/PH为0.8/1.5、膜厚为80μm的条件下,膜通量可达65.86L/(m2·h) | [ |
PVDF膜 | 蚀刻-电喷雾协同技术使用Al2O3纳米颗粒对PVDF膜改性制成有微/纳凹结构的亲/疏水Janus膜 | 相较PVDF膜和双疏膜处理高盐含油废水时30min就被污染,Janus膜可连续稳定运行45h仍未被污染 | [ |
膜蒸馏形式 | 强化形式 | 结果 | 参考文献 |
---|---|---|---|
DCMD | 基于三周期极小曲面(TPMS)的具有横向交联结构(tCLP)的聚丙烯垫片 | 以1900mg/L的硫酸钙为料液,温差为30℃条件下,效果较好的tCLP垫片能使得通量增加50%,但会增加压降 | [ |
DCMD | 基于TPMS的tCLP和Gyroid垫片 | tCLP和Gyroid垫片都可以显著提升MD的性能,但都不可避免地使压降变大;Gyroid垫片具有更好的缓解有机污染性能,但tCLP对通量的提升 效果更显著 | [ |
DCMD | 无纺布网隔板 | 在较高的流速下,填充的无纺布隔板使通量增加7%~19%。增加垫片对进料通道的通量增强可达21%~33%。在更高的温度下,垫片对温度极化的改善更明显 | [ |
DCMD | 六种有不同流动攻角和格栅夹角三维扰流层 | 曲线型攻角为45°和夹角为90°的扰流层强化效果最好,能使膜通量提升73.99% | [ |
AGMD | 螺旋式和波浪式中空纤维膜 | 50℃时可分别提升7%和4%的通量;75℃时可分别提升40%和36%的通量 | [ |
膜蒸馏形式 | 强化形式 | 结果 | 参考文献 |
---|---|---|---|
DCMD | 基于三周期极小曲面(TPMS)的具有横向交联结构(tCLP)的聚丙烯垫片 | 以1900mg/L的硫酸钙为料液,温差为30℃条件下,效果较好的tCLP垫片能使得通量增加50%,但会增加压降 | [ |
DCMD | 基于TPMS的tCLP和Gyroid垫片 | tCLP和Gyroid垫片都可以显著提升MD的性能,但都不可避免地使压降变大;Gyroid垫片具有更好的缓解有机污染性能,但tCLP对通量的提升 效果更显著 | [ |
DCMD | 无纺布网隔板 | 在较高的流速下,填充的无纺布隔板使通量增加7%~19%。增加垫片对进料通道的通量增强可达21%~33%。在更高的温度下,垫片对温度极化的改善更明显 | [ |
DCMD | 六种有不同流动攻角和格栅夹角三维扰流层 | 曲线型攻角为45°和夹角为90°的扰流层强化效果最好,能使膜通量提升73.99% | [ |
AGMD | 螺旋式和波浪式中空纤维膜 | 50℃时可分别提升7%和4%的通量;75℃时可分别提升40%和36%的通量 | [ |
工艺 | 能量回收 形式 | 参数 | 膜通量/L·m-2·h-1 | 造水比 | 其他 | 参考 文献 |
---|---|---|---|---|---|---|
三级并联和三级串联AGMD | 内部回收 | 热料液温度90℃,原料液温度20℃,气隙厚度4.0mm | 并联时为单级的3倍;串联时为单级的2.6倍 | — | 并联的能量利用率为0.6,串联为0.45 | [ |
能量回收AGMD组件 | 内部回收 | 热料液温度90℃,原料液温度40℃,气隙厚度0.5mm,中空纤维膜/换热管为2/1 | 3.1 | 4.3 | 热效率80%以上 | [ |
用于海水深度浓缩的多效膜蒸馏 | 内部回收 | 热料液温度95℃,原料液温度30℃,进料流量40L/h,料液浓度34g/L | 3.61~6.07 | 4.96~13.2 | 截留率99.9% | [ |
多效膜蒸馏用于氢氧化钠溶液浓缩 | 内部回收 | 热料液温度95℃,原料液温度30℃,进料流量30L/h,料液浓度200g/L | 3.05 | 5.04 | 截留率99.9% | [ |
耦合热泵型三级减压多效膜蒸馏 | 外部回收 | 热料液温度70℃,原料液温度30℃,料液流量104L/h,冷却水流量54L/h,热泵COP为3.11 | 2.26 | 3.65 | — | [ |
工艺 | 能量回收 形式 | 参数 | 膜通量/L·m-2·h-1 | 造水比 | 其他 | 参考 文献 |
---|---|---|---|---|---|---|
三级并联和三级串联AGMD | 内部回收 | 热料液温度90℃,原料液温度20℃,气隙厚度4.0mm | 并联时为单级的3倍;串联时为单级的2.6倍 | — | 并联的能量利用率为0.6,串联为0.45 | [ |
能量回收AGMD组件 | 内部回收 | 热料液温度90℃,原料液温度40℃,气隙厚度0.5mm,中空纤维膜/换热管为2/1 | 3.1 | 4.3 | 热效率80%以上 | [ |
用于海水深度浓缩的多效膜蒸馏 | 内部回收 | 热料液温度95℃,原料液温度30℃,进料流量40L/h,料液浓度34g/L | 3.61~6.07 | 4.96~13.2 | 截留率99.9% | [ |
多效膜蒸馏用于氢氧化钠溶液浓缩 | 内部回收 | 热料液温度95℃,原料液温度30℃,进料流量30L/h,料液浓度200g/L | 3.05 | 5.04 | 截留率99.9% | [ |
耦合热泵型三级减压多效膜蒸馏 | 外部回收 | 热料液温度70℃,原料液温度30℃,料液流量104L/h,冷却水流量54L/h,热泵COP为3.11 | 2.26 | 3.65 | — | [ |
案例 | 参数 | 膜通量/L·m-2·h-1 | 造水比 | 脱盐率/% | 参考文献 |
---|---|---|---|---|---|
太阳能AGMD海水淡化系统 | 料液、冷却液流速:15~20L/min 料液温度:40~85℃ 冷凝液温度:20~80℃ | 最高6.5 | 0.28~0.79 | >99 | [ |
螺旋缠绕式气隙膜蒸馏组件 (SW-AGMD-HF)用于海水淡化 | 料液温度:70~90℃ 冷却液温度:25~45℃ 料液流量:20~50L/h | 5.87 | 5.37 | >99 | [ |
太阳能中空纤维AGMD海水淡化装置 | 料液温度:50~80℃ 冷却液温度:25℃ 料液流量:50L/h 太阳能集热面积:2.38m2 膜面积:0.6m2 | 晴天最大5.1 多云最大2.4 | 1.1~3.2 | >99 | [ |
有隔网的螺旋缠绕式中空纤维膜蒸馏组件 用于海水淡化 | 料液温度:30~80℃ 冷却液温度:25℃ | 最高6.1 | 5.8 | >99 | [ |
内部换热式多效气隙式膜蒸馏组件 用于海水淡化 | 料液温度:90℃ 冷却温度:30℃ NaCl质量分数:3% | 最大6.8 | 6.2~12.5 | >99 | [ |
案例 | 参数 | 膜通量/L·m-2·h-1 | 造水比 | 脱盐率/% | 参考文献 |
---|---|---|---|---|---|
太阳能AGMD海水淡化系统 | 料液、冷却液流速:15~20L/min 料液温度:40~85℃ 冷凝液温度:20~80℃ | 最高6.5 | 0.28~0.79 | >99 | [ |
螺旋缠绕式气隙膜蒸馏组件 (SW-AGMD-HF)用于海水淡化 | 料液温度:70~90℃ 冷却液温度:25~45℃ 料液流量:20~50L/h | 5.87 | 5.37 | >99 | [ |
太阳能中空纤维AGMD海水淡化装置 | 料液温度:50~80℃ 冷却液温度:25℃ 料液流量:50L/h 太阳能集热面积:2.38m2 膜面积:0.6m2 | 晴天最大5.1 多云最大2.4 | 1.1~3.2 | >99 | [ |
有隔网的螺旋缠绕式中空纤维膜蒸馏组件 用于海水淡化 | 料液温度:30~80℃ 冷却液温度:25℃ | 最高6.1 | 5.8 | >99 | [ |
内部换热式多效气隙式膜蒸馏组件 用于海水淡化 | 料液温度:90℃ 冷却温度:30℃ NaCl质量分数:3% | 最大6.8 | 6.2~12.5 | >99 | [ |
案例 | 参数 | 膜通量/L·m-2·h-1 | 处理效果 | 参考文献 |
---|---|---|---|---|
AGMD处理含酸浓缩废水 | 料液温度:40~65℃ 冷却温度:21℃ | 2.5以上 | 总体截留率:99.68% 水回收率:75% | [ |
AGMD处理含铀废水 | 料液温度:50~70℃ 冷却温度:20℃±1℃ | 3.0~9.0 | 铀截留率:99% 氟截留率:98% | [ |
AGMD处理电厂脱硫废水 | 进料温度:60~78℃ 进料流速:30L/h | 1.64~4.22 | 盐截留率:99.8%~100% | [ |
AGMD模拟处理印染废水 | 料液温度:70℃ 冷却温度:20℃ | 11.7~12.6 | 日落黄、玫瑰红染料以及十二烷基硫酸钠表面活性剂的去除率达100%且可将颜色完全去除 | [ |
AGMD处理模拟含放射性废水(Cs+、Sr2+、Co2+、UO22+) | 料液温度:60~90℃ 料液流速:80~180L/h 气隙厚度:3~15mm | 4.79~16.24 | 各种操作条件下的Cs+、Sr2+、Co2+、UO22+去除率均能达到99%以上。在72h浓缩实验中,膜通量呈先升后降低趋势,但是对各种离子的去除率都稳定在99.99% | [ |
多效膜蒸馏处理预处理后的炼油废水浓水 | 外部热源为97℃热水 进料流量:40L/h 进料温度:25℃ | 4.5~6.5 | 淡水回收率达95%,出水电导率仅有5.9~7.2μS/cm且CODCr小于45mg/L,造水比为6.8~10.2 | [ |
多效膜蒸馏处理电镀反渗透浓水 | 料液温度:65~85℃ 料液流速:15~55L/h 冷却液温度:25~45℃ 冷却液流速:25~45L/h | 最高5.136 | 产水电导率<50μS/cm,浊度<15mg/L,色度<2NTU,脱盐率>99%,出水能达到国家污水综合排放二级标准 | [ |
案例 | 参数 | 膜通量/L·m-2·h-1 | 处理效果 | 参考文献 |
---|---|---|---|---|
AGMD处理含酸浓缩废水 | 料液温度:40~65℃ 冷却温度:21℃ | 2.5以上 | 总体截留率:99.68% 水回收率:75% | [ |
AGMD处理含铀废水 | 料液温度:50~70℃ 冷却温度:20℃±1℃ | 3.0~9.0 | 铀截留率:99% 氟截留率:98% | [ |
AGMD处理电厂脱硫废水 | 进料温度:60~78℃ 进料流速:30L/h | 1.64~4.22 | 盐截留率:99.8%~100% | [ |
AGMD模拟处理印染废水 | 料液温度:70℃ 冷却温度:20℃ | 11.7~12.6 | 日落黄、玫瑰红染料以及十二烷基硫酸钠表面活性剂的去除率达100%且可将颜色完全去除 | [ |
AGMD处理模拟含放射性废水(Cs+、Sr2+、Co2+、UO22+) | 料液温度:60~90℃ 料液流速:80~180L/h 气隙厚度:3~15mm | 4.79~16.24 | 各种操作条件下的Cs+、Sr2+、Co2+、UO22+去除率均能达到99%以上。在72h浓缩实验中,膜通量呈先升后降低趋势,但是对各种离子的去除率都稳定在99.99% | [ |
多效膜蒸馏处理预处理后的炼油废水浓水 | 外部热源为97℃热水 进料流量:40L/h 进料温度:25℃ | 4.5~6.5 | 淡水回收率达95%,出水电导率仅有5.9~7.2μS/cm且CODCr小于45mg/L,造水比为6.8~10.2 | [ |
多效膜蒸馏处理电镀反渗透浓水 | 料液温度:65~85℃ 料液流速:15~55L/h 冷却液温度:25~45℃ 冷却液流速:25~45L/h | 最高5.136 | 产水电导率<50μS/cm,浊度<15mg/L,色度<2NTU,脱盐率>99%,出水能达到国家污水综合排放二级标准 | [ |
案例 | 参数 | 膜通量和造水比 | 处理效果 | 参考文献 |
---|---|---|---|---|
多效膜蒸馏装置浓缩硫酸盐、盐酸盐等16种无机盐水溶液 | 料液温度:90℃ 冷凝液温度:30℃ 冷凝液流速:30L/h 料液浓度:0.5%~40% | 膜通量和造水比最高达 4.5L/(m2·h)和11.0,但均随着 处理时间的升高而下降 | 实验全程截留率在99.99%以上,电导率保持在200μS/cm以下,当料液浓度达到18%时16种溶液的膜通量和造水比都可保持在2.30L/(m2·h)和6.9以上 | [ |
多效膜蒸馏处理预处理后的炼油废水浓水 | 外部热源为97℃热水 进料流量:40L/h 进料温度:25℃ | 膜通量:4.5~6.5L/(m2·h) 造水比:6.8~10.2 | 可将废水浓缩19倍以上 | [ |
AGMD浓缩西瓜汁、梨汁、苹果汁和柚子汁 | 进料温度:70℃ | 膜通量:3L/(m2·h) 造水比:8.0 | 可将果汁从8°Brix浓缩到55°Brix且果汁风味成分保存良好 | [ |
AGMD浓缩氢氧化钠溶液 | 进料温度:70~95℃ 冷却液温度:20~45℃ 料液流量:6~26L/h | 膜通量:3.9~7.7L/(m2·h) 造水比:1.7~2.7 | 可将NaOH溶液浓缩9.5倍,截留率可达99.9%,但在浓缩过程中膜通量和造水比会逐渐下降 | [ |
多效膜蒸馏浓缩中药提取液 | 热料液温度:70℃ 冷料液温度:30℃ 料液流量:30L/h | 膜通量:3L/(m2·h) 造水比:7.0 | 长期操作稳定性良好,可将各种重要提取液浓缩16倍以上,膜通量和造水比仍可达到1.6L/(m2·h)和5~5.55,且有效成分保留完整 | [ |
案例 | 参数 | 膜通量和造水比 | 处理效果 | 参考文献 |
---|---|---|---|---|
多效膜蒸馏装置浓缩硫酸盐、盐酸盐等16种无机盐水溶液 | 料液温度:90℃ 冷凝液温度:30℃ 冷凝液流速:30L/h 料液浓度:0.5%~40% | 膜通量和造水比最高达 4.5L/(m2·h)和11.0,但均随着 处理时间的升高而下降 | 实验全程截留率在99.99%以上,电导率保持在200μS/cm以下,当料液浓度达到18%时16种溶液的膜通量和造水比都可保持在2.30L/(m2·h)和6.9以上 | [ |
多效膜蒸馏处理预处理后的炼油废水浓水 | 外部热源为97℃热水 进料流量:40L/h 进料温度:25℃ | 膜通量:4.5~6.5L/(m2·h) 造水比:6.8~10.2 | 可将废水浓缩19倍以上 | [ |
AGMD浓缩西瓜汁、梨汁、苹果汁和柚子汁 | 进料温度:70℃ | 膜通量:3L/(m2·h) 造水比:8.0 | 可将果汁从8°Brix浓缩到55°Brix且果汁风味成分保存良好 | [ |
AGMD浓缩氢氧化钠溶液 | 进料温度:70~95℃ 冷却液温度:20~45℃ 料液流量:6~26L/h | 膜通量:3.9~7.7L/(m2·h) 造水比:1.7~2.7 | 可将NaOH溶液浓缩9.5倍,截留率可达99.9%,但在浓缩过程中膜通量和造水比会逐渐下降 | [ |
多效膜蒸馏浓缩中药提取液 | 热料液温度:70℃ 冷料液温度:30℃ 料液流量:30L/h | 膜通量:3L/(m2·h) 造水比:7.0 | 长期操作稳定性良好,可将各种重要提取液浓缩16倍以上,膜通量和造水比仍可达到1.6L/(m2·h)和5~5.55,且有效成分保留完整 | [ |
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