无机材料学报 ›› 2022, Vol. 37 ›› Issue (10): 1065-1072.DOI: 10.15541/jim20220020 CSTR: 32189.14.10.15541/jim20220020
        
               		陈亚玲1,2( ), 舒松1,2, 王劭鑫1,2, 李建军1,2(
), 舒松1,2, 王劭鑫1,2, 李建军1,2( )
)
                  
        
        
        
        
    
收稿日期:2022-01-13
									
				
											修回日期:2022-04-14
									
				
									
				
											出版日期:2022-10-20
									
				
											网络出版日期:2022-04-26
									
			通讯作者:
					李建军, 教授. E-mail: jjli@scu.edu.cn作者简介:陈亚玲(1997-), 女, 硕士研究生. E-mail: chenyaling@stu.scu.edu.cn
				
							基金资助:
        
               		CHEN Yaling1,2( ), SHU Song1,2, WANG Shaoxin1,2, LI Jianjun1,2(
), SHU Song1,2, WANG Shaoxin1,2, LI Jianjun1,2( )
)
			  
			
			
			
                
        
    
Received:2022-01-13
									
				
											Revised:2022-04-14
									
				
									
				
											Published:2022-10-20
									
				
											Online:2022-04-26
									
			Contact:
					LI Jianjun, professor. E-mail: jjli@scu.edu.cnAbout author:CHEN Yaling (1997-), female, Master candidate. E-mail: chenyaling@stu.scu.edu.cn				
							Supported by:摘要:
低温选择性催化还原(SCR)脱硝是工业烟气末端治理的重要技术, 强化催化剂硫抗性是低温SCR领域内亟待解决的问题。本研究以羟基磷灰石(HAP)为载体、Mn为活性组分通过共沉淀法成功合成了Mn-HAP低温(100~200℃)脱硝催化剂, 探究了其脱硝性能及金属硫酸盐和硫酸铵的中毒特性。结果表明: 以HAP作为活性组分Mn的载体能一定程度上提高催化剂的抗硫性。当反应温度为140 ℃时, SCR催化剂脱硝效率达到100%, 金属硫酸盐相较硫酸铵对催化剂低温脱硝活性的影响更显著, 120 ℃时脱硝效率分别降低37.40%和8.83%。不同手段分析表明, 不同表面硫物种均会不同程度地降低催化剂比表面积并改变活性Mn氧化态。金属硫酸盐显著降低Mn4+/Mn比例是造成催化剂失活的主要原因。
中图分类号:
陈亚玲, 舒松, 王劭鑫, 李建军. Mn-HAP基低温SCR催化剂的制备及抗硫中毒性能[J]. 无机材料学报, 2022, 37(10): 1065-1072.
CHEN Yaling, SHU Song, WANG Shaoxin, LI Jianjun. Mn-HAP SCR Catalyst: Preparation and Sulfur Resistance[J]. Journal of Inorganic Materials, 2022, 37(10): 1065-1072.
 
																													图3 (a)CPF、CPM、CPA和HAP的SCR活性以及CPF的抗硫性测试和(b)CPF稳定性测试图
Fig. 3 (a) SCR activity of CPF, CPM, CPA, and HAP, and sulfur resistance test of CPF and (b) stability test of CPF Colorful figures are available on website
| Catalyst | Preparation method | NO conversion/% | Temperature and condition | Ref. | 
|---|---|---|---|---|
| Mn-HAP | Co-preparation | 62.60 | 140 ℃, 200×10-6 SO2, 2 h | This research | 
| NB-C-P | Hydrothermal | 45.00 | 150 ℃, 250×10-6 SO2, 2 h | [ | 
| MnO2 | Oxalic acid co-precipitation | 17.65 | 150 ℃, 200×10-6 SO2, 2 h | [ | 
| MnCrOx | Hydrothermal redox reaction | 37.46 | 150 ℃, 50×10-6 SO2, 2 h | [ | 
表1 不同催化剂活性对比
Table 1 Activity comparison of different catalysts
| Catalyst | Preparation method | NO conversion/% | Temperature and condition | Ref. | 
|---|---|---|---|---|
| Mn-HAP | Co-preparation | 62.60 | 140 ℃, 200×10-6 SO2, 2 h | This research | 
| NB-C-P | Hydrothermal | 45.00 | 150 ℃, 250×10-6 SO2, 2 h | [ | 
| MnO2 | Oxalic acid co-precipitation | 17.65 | 150 ℃, 200×10-6 SO2, 2 h | [ | 
| MnCrOx | Hydrothermal redox reaction | 37.46 | 150 ℃, 50×10-6 SO2, 2 h | [ | 
| Sample | Specific area/ (m2·g-1) | Pore volume/ (cm3·g-1) | Average pore size/nm | 
|---|---|---|---|
| CPF | 153.6 | 0.5500 | 13.49 | 
| CPM | 117.3 | 0.4600 | 14.11 | 
| CPA | 133.2 | 0.4300 | 11.57 | 
表2 新鲜催化剂与中毒催化剂物理参数
Table 2 Physical parameters of fresh catalysts and toxic catalysts
| Sample | Specific area/ (m2·g-1) | Pore volume/ (cm3·g-1) | Average pore size/nm | 
|---|---|---|---|
| CPF | 153.6 | 0.5500 | 13.49 | 
| CPM | 117.3 | 0.4600 | 14.11 | 
| CPA | 133.2 | 0.4300 | 11.57 | 
| Sample | O | Mn | ||||
|---|---|---|---|---|---|---|
| Olatt/O | Oads/O | Oads/Olatt | Mn2+/Mn | Mn3+/Mn | Mn4+/Mn | |
| CPF | 0.9050 | 0.0950 | 0.1050 | 0.06510 | 0.1670 | 0.7300 | 
| CPM | 0.9210 | 0.0790 | 0.0860 | 0.10000 | 0.5900 | 0.3100 | 
| CPA | 0.8760 | 0.1230 | 0.1410 | 0.13500 | 0.2240 | 0.6410 | 
表3 新鲜催化剂与中毒催化剂表面Mn和O的XPS分析结果
Table 3 XPS results of Mn and O on the surface of fresh catalysts and toxic catalysts
| Sample | O | Mn | ||||
|---|---|---|---|---|---|---|
| Olatt/O | Oads/O | Oads/Olatt | Mn2+/Mn | Mn3+/Mn | Mn4+/Mn | |
| CPF | 0.9050 | 0.0950 | 0.1050 | 0.06510 | 0.1670 | 0.7300 | 
| CPM | 0.9210 | 0.0790 | 0.0860 | 0.10000 | 0.5900 | 0.3100 | 
| CPA | 0.8760 | 0.1230 | 0.1410 | 0.13500 | 0.2240 | 0.6410 | 
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