化工进展 ›› 2021, Vol. 40 ›› Issue (2): 789-799.DOI: 10.16085/j.issn.1000-6613.2020-0722
孟宪政1(), 庄瑞杰1, 于庆君1,2(), 唐晓龙1,2(), 易红宏1,2, 冯勇超1, 隗晶慧1, 陈超祺1
收稿日期:
2020-04-30
修回日期:
2020-06-07
出版日期:
2021-02-05
发布日期:
2021-02-09
通讯作者:
于庆君,唐晓龙
作者简介:
孟宪政(1997—),男,硕士研究生,研究方向为大气污染控制。E-mail:基金资助:
Xianzheng MENG1(), Ruijie ZHUANG1, Qingjun YU1,2(), Xiaolong TANG1,2(), Honghong YI1,2, Yongchao FENG1, Jinghui WEI1, Chaoqi CHEN1
Received:
2020-04-30
Revised:
2020-06-07
Online:
2021-02-05
Published:
2021-02-09
Contact:
Qingjun YU,Xiaolong TANG
摘要:
制药行业在我国快速发展,带来经济增长与生活便利的同时也带来了大量挥发性有机污染物(VOCs)的排放。针对制药行业废气排放量大、排放节点多、污染物种类复杂等特点,催化燃烧因经济环保、应用灵活,成为处理制药VOCs的合适选择。本文总结了制药行业排放的典型VOCs及常见医用药品生产过程中的特征污染物,并着重从催化燃烧催化材料研发及应用的角度,总结了近年来制药行业典型VOCs催化燃烧技术的研究现状,同时对我国制药行业有机废气治理作了展望,即需进一步加深制药行业VOCs排放特征、VOCs实验室治理等基础研究来保证实际治理过程中的经济有效性;同时在原有催化氧化催化剂研究的基础上,研发多技术耦合工艺,实现制药行业废气的达标排放。
中图分类号:
孟宪政, 庄瑞杰, 于庆君, 唐晓龙, 易红宏, 冯勇超, 隗晶慧, 陈超祺. 制药行业有机废气催化燃烧研究进展[J]. 化工进展, 2021, 40(2): 789-799.
Xianzheng MENG, Ruijie ZHUANG, Qingjun YU, Xiaolong TANG, Honghong YI, Yongchao FENG, Jinghui WEI, Chaoqi CHEN. Research progress in catalytic combustion of organic waste gas in pharmaceutical industry[J]. Chemical Industry and Engineering Progress, 2021, 40(2): 789-799.
制药类别 | 废气产生节点 | 药物种类 | 特征污染物 | 排放特征 | 文献 |
---|---|---|---|---|---|
发酵类 | ①生物发酵尾气;②提取过程有机溶剂的挥发;③污水处理站废气以及菌渣等固废废气[ | 青霉素 | 正己烷、乙酸丁酯、丁醇 | 污染物种类多、排放量大、排放不稳定、多为无组织排放[ | [ |
维生素B12 | 丙酮 | [ | |||
维生素C | 乙酸乙酯、乙酸丁酯、丙酮 | [ | |||
生霉素 | 乙酸乙酯、乙酸丁酯、丙酮 | [ | |||
化学合成类 | ①合成过程中有机溶剂挥发;②提取和精制过程中有机溶媒挥发;③干燥过程中的粉尘和有机溶剂。还包括企业污水处理站和固废废气[ | 头孢克洛 | 丙酮、二氯甲烷 | [ | |
阿莫西林 | 丙酮、二氯甲烷、三乙胺 | [ | |||
氨苄西林 | 二氯甲烷、丙酮 | [ | |||
盐酸克林霉素 | 乙醇、丙酮 | [ |
表1 发酵类与化学合成类制药特征污染物
制药类别 | 废气产生节点 | 药物种类 | 特征污染物 | 排放特征 | 文献 |
---|---|---|---|---|---|
发酵类 | ①生物发酵尾气;②提取过程有机溶剂的挥发;③污水处理站废气以及菌渣等固废废气[ | 青霉素 | 正己烷、乙酸丁酯、丁醇 | 污染物种类多、排放量大、排放不稳定、多为无组织排放[ | [ |
维生素B12 | 丙酮 | [ | |||
维生素C | 乙酸乙酯、乙酸丁酯、丙酮 | [ | |||
生霉素 | 乙酸乙酯、乙酸丁酯、丙酮 | [ | |||
化学合成类 | ①合成过程中有机溶剂挥发;②提取和精制过程中有机溶媒挥发;③干燥过程中的粉尘和有机溶剂。还包括企业污水处理站和固废废气[ | 头孢克洛 | 丙酮、二氯甲烷 | [ | |
阿莫西林 | 丙酮、二氯甲烷、三乙胺 | [ | |||
氨苄西林 | 二氯甲烷、丙酮 | [ | |||
盐酸克林霉素 | 乙醇、丙酮 | [ |
催化剂组成 | 污染物 | 浓度/ppm | GHSV/WHSV | 反应温度/℃ | 催化效率/% | 参考文献 |
---|---|---|---|---|---|---|
Ru/TiO2 | 二氯甲烷 | 1000 | 30000h-1 | 335 | 100 | [ |
Pd-Au/TiO2 | 甲苯 | 1000 | 60000mL·g-1·h-1 | 210 | 90 | [ |
Pt/Al2O3 | 二氯甲烷 | 500 | 143790h-1 | 450 | 100 | [ |
Ag/CeO2 | 乙酸乙酯 | 500 | 60000mL·g-1·h-1 | 197 | 90 | [ |
Pt/CeO2-Al2O3 | 二氯甲烷 | 3000 | 15000h-1 | 312 | 50 | [ |
Pd-Mn/TiO2 | 丙酮 | 1000 | 30000mL·g-1·h-1 | 259 | 100 | [ |
Pd/ZSM-5 | 甲苯 | 1500 | 26000h-1 | 272 | 90 | [ |
Pt/MOR | 甲苯 | 1000 | 60000mL·g-1·h-1 | 190 | 90 | [ |
Pt/ZSM-5 | 甲苯 | 500 | 80000mL·g-1·h-1 | 159 | 90 | [ |
Pt/Beta | 甲苯 | 1000 | 30000mL·g-1·h-1 | 189 | 98 | [ |
表2 近年用于典型制药有机废气催化燃烧的贵金属催化剂催化性能
催化剂组成 | 污染物 | 浓度/ppm | GHSV/WHSV | 反应温度/℃ | 催化效率/% | 参考文献 |
---|---|---|---|---|---|---|
Ru/TiO2 | 二氯甲烷 | 1000 | 30000h-1 | 335 | 100 | [ |
Pd-Au/TiO2 | 甲苯 | 1000 | 60000mL·g-1·h-1 | 210 | 90 | [ |
Pt/Al2O3 | 二氯甲烷 | 500 | 143790h-1 | 450 | 100 | [ |
Ag/CeO2 | 乙酸乙酯 | 500 | 60000mL·g-1·h-1 | 197 | 90 | [ |
Pt/CeO2-Al2O3 | 二氯甲烷 | 3000 | 15000h-1 | 312 | 50 | [ |
Pd-Mn/TiO2 | 丙酮 | 1000 | 30000mL·g-1·h-1 | 259 | 100 | [ |
Pd/ZSM-5 | 甲苯 | 1500 | 26000h-1 | 272 | 90 | [ |
Pt/MOR | 甲苯 | 1000 | 60000mL·g-1·h-1 | 190 | 90 | [ |
Pt/ZSM-5 | 甲苯 | 500 | 80000mL·g-1·h-1 | 159 | 90 | [ |
Pt/Beta | 甲苯 | 1000 | 30000mL·g-1·h-1 | 189 | 98 | [ |
催化剂组成 | 污染物 | 浓度/ppm | GHSV/WHSV | 反应温度/℃ | 催化效率/% | 参考文献 |
---|---|---|---|---|---|---|
Cu/分子筛-不锈钢纤维 | 丙酮 | 1500 | 13221h-1 | 300 | 90 | [ |
CuO/ZSM-5 | 乙酸乙酯 | 1500 | 15000h-1 | 235 | 90 | [ |
MnOx/TiO2纳米线 | 丙酮 | 500 | 360000mL·g-1·h-1 | 290 | 90 | [ |
表3 近年用于典型制药有机废气催化燃烧的单一金属氧化物催化剂催化性能
催化剂组成 | 污染物 | 浓度/ppm | GHSV/WHSV | 反应温度/℃ | 催化效率/% | 参考文献 |
---|---|---|---|---|---|---|
Cu/分子筛-不锈钢纤维 | 丙酮 | 1500 | 13221h-1 | 300 | 90 | [ |
CuO/ZSM-5 | 乙酸乙酯 | 1500 | 15000h-1 | 235 | 90 | [ |
MnOx/TiO2纳米线 | 丙酮 | 500 | 360000mL·g-1·h-1 | 290 | 90 | [ |
催化剂组成 | 污染物 | 浓度/ppm | GHSV/WHSV | 反应温度/℃ | 催化效率/% | 参考文献 |
---|---|---|---|---|---|---|
CeO2-Co3O4 | 乙酸乙酯 | 1000 | 60000h-1 | 260 | 100 | [ |
Cs/锰钾矿 | 乙酸乙酯 | 1600 | 16000h-1 | 200 | 100 | [ |
Fe-Mn | 甲苯 | 10000 | 20000mL·g-1·h-1 | 282 | 80 | [ |
CoCr2O4 | 二氯甲烷 | 3000 | 15000h-1 | 210 | 50 | [ |
钴铝水滑石 | 丙酮 | 1000 | 33000mL·g-1·h-1 | 250 | 100 | [ |
Co3O4/泡沫镍 | 丙酮 | 580 | 17000mL·g-1·h-1 | 177 | 90 | [ |
CuCexZr1-xOy/ZSM-5 | 乙酸乙酯 | — | 24000h-1 | 270 | 100 | [ |
锰铝水滑石 | 丙酮 | 258 | 18000mL·g-1·h-1 | 170 | 100 | [ |
CuCo2O4空心球 | 丙酮 | 1000 | 93000mL·g-1·h-1 | 200 | 100 | [ |
表4 近年用于典型制药有机废气催化燃烧的复合金属氧化物催化剂催化性能
催化剂组成 | 污染物 | 浓度/ppm | GHSV/WHSV | 反应温度/℃ | 催化效率/% | 参考文献 |
---|---|---|---|---|---|---|
CeO2-Co3O4 | 乙酸乙酯 | 1000 | 60000h-1 | 260 | 100 | [ |
Cs/锰钾矿 | 乙酸乙酯 | 1600 | 16000h-1 | 200 | 100 | [ |
Fe-Mn | 甲苯 | 10000 | 20000mL·g-1·h-1 | 282 | 80 | [ |
CoCr2O4 | 二氯甲烷 | 3000 | 15000h-1 | 210 | 50 | [ |
钴铝水滑石 | 丙酮 | 1000 | 33000mL·g-1·h-1 | 250 | 100 | [ |
Co3O4/泡沫镍 | 丙酮 | 580 | 17000mL·g-1·h-1 | 177 | 90 | [ |
CuCexZr1-xOy/ZSM-5 | 乙酸乙酯 | — | 24000h-1 | 270 | 100 | [ |
锰铝水滑石 | 丙酮 | 258 | 18000mL·g-1·h-1 | 170 | 100 | [ |
CuCo2O4空心球 | 丙酮 | 1000 | 93000mL·g-1·h-1 | 200 | 100 | [ |
催化剂组成 | 污染物 | 浓度/ppm | GHSV/WHSV | 反应温度/℃ | 催化效率/% | 参考文献 |
---|---|---|---|---|---|---|
核壳Al2O3@Pd-CoAlO | 甲苯 | 2000 | 60000mL·g-1·h-1 | 207 | 90 | [ |
Mn1.20Co1.80O4空心球 | 丙酮 | 1000 | 93000mL·g-1·h-1 | 140 | 100 | [ |
蛋黄壳状CoCrOx | 二氯甲烷 | 1000 | 43750mL·g-1·h-1 | 325 | 90 | [ |
MnOx-CeO2(MOF模板) | 乙酸乙酯 | 500 | 60000mL·g-1·h-1 | 210 | 99 | [ |
CeCuOx(MOF前体) | 丙酮 | 500 | 23000h-1 | 186 | 90 | [ |
表5 近年用于典型制药有机废气催化燃烧的特殊结构金属氧化物催化剂催化性能
催化剂组成 | 污染物 | 浓度/ppm | GHSV/WHSV | 反应温度/℃ | 催化效率/% | 参考文献 |
---|---|---|---|---|---|---|
核壳Al2O3@Pd-CoAlO | 甲苯 | 2000 | 60000mL·g-1·h-1 | 207 | 90 | [ |
Mn1.20Co1.80O4空心球 | 丙酮 | 1000 | 93000mL·g-1·h-1 | 140 | 100 | [ |
蛋黄壳状CoCrOx | 二氯甲烷 | 1000 | 43750mL·g-1·h-1 | 325 | 90 | [ |
MnOx-CeO2(MOF模板) | 乙酸乙酯 | 500 | 60000mL·g-1·h-1 | 210 | 99 | [ |
CeCuOx(MOF前体) | 丙酮 | 500 | 23000h-1 | 186 | 90 | [ |
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