Biomass-Waste-Derived Silica for Solvent-Lean Cu-SSZ-13 Porous Catalysts in NH3-SCR NOx Remediation
Abstract
1. Introduction
2. Results and Discussion
2.1. Structural, Compositional, and Functional Characteristics of the RHA/MK-Derived Cu-SSZ-13 Catalysts
2.1.1. CHA Phase Formation by XRD
2.1.2. Framework Aluminum Environments by 27Al MAS NMR
2.1.3. Silicate Framework Environments by 29Si MAS NMR
2.1.4. Cu-Related Optical Response by UV–Vis DRS
2.1.5. NH3-Interaction Behavior by NH3-TPD
2.1.6. Catalytic Performance in NH3-SCR Fixed-Bed Tests
2.1.7. Nitrogen-Product Response and N2O Formation
2.2. Integrated Structure–Property–Function Relationships
3. Materials and Methods
3.1. Starting Materials
3.2. Experimental Design and Synthesis Matrix
3.3. Gel Preparation and Alkaline Activation
3.4. Cu-Containing Crystallization Conditions
3.5. Dry-Gel Formation and Vapor-Assisted Crystallization
3.6. Calcination and Conversion to the Protonic Form
3.7. Post-Synthetic Cu Ion Exchange and Compositional Analysis
3.8. Integrated Characterization Strategy
3.9. NH3-SCR Catalytic Tests
3.10. Hydrothermal Aging
4. Conclusions
Supplementary Materials
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Acknowledgments
Conflicts of Interest
References
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| Sample | Al(IV) Region (%) | Intermediate Region (%) | Al(VI) Region (%) | δmax Al(IV) (ppm) | δmax Intermediate (ppm) | δmax Al(VI) (ppm) |
|---|---|---|---|---|---|---|
| S1 | 83.06 | 8.38 | 8.56 | 55.0 | 28.0 | −0.1 |
| S2 | 84.68 | 7.65 | 7.66 | 55.1 | 28.1 | 0.3 |
| S3 | 82.40 | 8.85 | 8.75 | 54.8 | 28.2 | 0.1 |
| S4 | 84.06 | 7.93 | 8.01 | 54.9 | 28.3 | 0.2 |
| S5 | 82.33 | 8.86 | 8.81 | 55.0 | 28.5 | 0.1 |
| S6 | 84.69 | 7.77 | 7.54 | 55.0 | 28.1 | −0.1 |
| S7 | 83.29 | 8.38 | 8.33 | 54.8 | 28.3 | −0.3 |
| S8 | 85.47 | 7.35 | 7.18 | 54.9 | 28.3 | −0.3 |
| Sample | Component Near −98 ppm (%) | Component Near −103 to −104 ppm (%) | Component Near −108 to −109 ppm (%) | Component Near −114 ppm (%) |
|---|---|---|---|---|
| S1 | 7.9 | 18.8 | 45.8 | 27.5 |
| S2 | 5.9 | 20.3 | 46.4 | 27.4 |
| S3 | 6.7 | 20.8 | 46.1 | 26.4 |
| S4 | 5.1 | 20.4 | 47.9 | 26.6 |
| S5 | 7.3 | 11.2 | 24.4 | 57.1 |
| S6 | 5.0 | 10.9 | 29.9 | 54.2 |
| S7 | 5.4 | 11.7 | 27.2 | 55.7 |
| S8 | 3.4 | 11.3 | 32.0 | 53.3 |
| Sample | Total Integrated Area (a.u.·°C) | Low-Temperature Contribution (%) | Intermediate-Temperature Contribution (%) | High-Temperature Contribution (%) | Tmax, Low-Temperature Region (°C) | Tmax, Intermediate-Temperature Region (°C) | Tmax, High-Temperature Region (°C) |
|---|---|---|---|---|---|---|---|
| S1 | 27.05 | 37.6 | 38.3 | 24.1 | 309.5 | 527.0 | 674.0 |
| S2 | 27.70 | 37.9 | 37.4 | 24.7 | 311.5 | 517.5 | 682.5 |
| S3 | 27.83 | 31.5 | 33.9 | 34.7 | 312.0 | 521.5 | 689.5 |
| S4 | 29.81 | 28.6 | 33.1 | 38.3 | 310.5 | 526.0 | 684.0 |
| S5 | 30.26 | 38.6 | 42.9 | 18.5 | 309.0 | 522.0 | — |
| S6 | 31.34 | 38.9 | 42.5 | 18.6 | 309.5 | 519.5 | — |
| S7 | 34.21 | 38.3 | 44.2 | 17.5 | 310.5 | 515.5 | — |
| S8 | 35.23 | 39.5 | 44.6 | 16.0 | 311.0 | 518.0 | — |
| Sample | T50 Fresh (°C) | T50 Aged (°C) | ΔT50 (°C) | Maximum NOx Conversion Fresh (%) | Maximum NOx Conversion Aged (%) | Retained Maximum NOx Conversion (%) |
|---|---|---|---|---|---|---|
| S1 | 237.6 | 269.9 | 32.4 | 93.3 | 88.6 | 94.9 |
| S2 | 221.6 | 263.5 | 41.9 | 95.3 | 89.1 | 93.5 |
| S3 | 268.3 | 302.4 | 34.1 | 91.8 | 83.7 | 91.1 |
| S4 | 201.3 | 266.6 | 65.3 | 97.0 | 89.2 | 91.9 |
| S5 | 248.0 | 283.0 | 35.0 | 92.4 | 87.4 | 94.6 |
| S6 | 241.0 | 278.4 | 37.4 | 93.1 | 87.5 | 94.0 |
| S7 | 278.4 | 312.8 | 34.4 | 89.9 | 82.1 | 91.3 |
| S8 | 238.4 | 280.6 | 42.2 | 93.6 | 87.7 | 93.6 |
| Sample | Final Si/Al Ratio | Final Cu Content (wt%) | Final Molar Cu/Al Ratio | Synthesis Condition/Sample Role |
|---|---|---|---|---|
| S1 | 12.3 | 2.32 | 0.22 | Cu-free crystallization, OSDA-free |
| S2 | 12.4 | 2.39 | 0.23 | Cu-containing crystallization, OSDA-free |
| S3 | 12.2 | 2.50 | 0.25 | Cu-free crystallization, OSDA-lean |
| S4 | 12.1 | 2.61 | 0.27 | Cu-containing crystallization, OSDA-lean |
| S5 | 24.8 | 1.50 | 0.23 | Cu-free crystallization, OSDA-free |
| S6 | 24.7 | 1.55 | 0.24 | Cu-containing crystallization, OSDA-free |
| S7 | 25.0 | 1.64 | 0.22 | Cu-free crystallization, OSDA-lean |
| S8 | 25.2 | 1.72 | 0.23 | Cu-containing crystallization, OSDA-lean |
| Catalyst/Study | Preparation Strategy and Synthesis Complexity | Representative NH3-SCR Performance | Comparison with the Present Work |
|---|---|---|---|
| S1–S8, present work | RHA/MK-derived route; solvent-lean VAC; OSDA-free or OSDA-lean formulations; common post-synthetic Cu ion exchange | Fresh T50 = 201.3–278.4 °C; maximum NOx conversion = 89.9–97.0% | Combines biomass-waste-derived silica, reduced or zero OSDA demand, and solvent-lean crystallization with substantial NH3-SCR functionality |
| Xie et al. [12] | One-pot Cu-SSZ-13 synthesis with direct Cu incorporation during synthesis | High NH3-SCR activity and N2 selectivity over approximately 150–550 °C | Earlier activation and broader high-performance temperature window than the present catalyst matrix, using an optimized one-pot synthesis route |
| Lv et al. [18] | Al-rich Cu-SSZ-13 prepared through different synthesis strategies; synthesis conditions tailored to control Al distribution and hydrothermal stability | High NH3-SCR activity together with strong hydrothermal stability; catalytic behavior strongly depended on synthesis route | Demonstrates that optimized control of synthesis and Al distribution can provide stronger catalytic and hydrothermal performance, although with a more specifically engineered preparation strategy |
| Robles et al. [19] | Post-synthetically treated SSZ-13 followed by Cu modification; additional post-synthesis processing steps | Effective NH3-SCR-DeNOx activity after structural modification and Cu incorporation | Shows that post-synthetic optimization can enhance catalytic functionality, but requires additional treatment steps after zeolite synthesis |
| Yang et al. [29] | Hard-template-assisted trans-crystallization synthesis of hierarchical Cu-SSZ-13; additional templating and trans-crystallization steps | Enhanced low-temperature NH3-SCR activity and improved hydrothermal stability | Superior low-temperature behavior achieved through hierarchical pore engineering, but with a more complex preparation sequence than the present VAC route |
| Wang et al. [35] | One-pot synthesis of Na+-free Cu-SSZ-13; direct preparation without a separate Na+-removal step | Strong NH3-SCR performance combined with hydrothermal stability | Representative efficient one-pot route with high catalytic performance and reduced post-synthesis ion-exchange requirements |
| Al Jabri et al. [36] | Dry-gel conversion synthesis of Cu/SSZ-13; low-liquid crystallization followed by Cu incorporation | High NH3-SCR performance and hydrothermal stability for the DGC-derived catalyst | Particularly relevant benchmark because it combines a low-liquid preparation strategy with high catalytic performance |
| Gao et al. [37] | Conventional SSZ-13 synthesis followed by controlled Cu ion exchange at different Cu loadings | High standard and fast NH3-SCR activity associated with Cu loading, location, and accessibility | Provides a fundamental high-performance structure–activity benchmark, although based on conventional zeolite preparation followed by controlled Cu exchange |
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Klunk, M.A.; Caetano, N.R.; Lorenzini, G.; Orbegoso, E.M.M. Biomass-Waste-Derived Silica for Solvent-Lean Cu-SSZ-13 Porous Catalysts in NH3-SCR NOx Remediation. Molecules 2026, 31, 3282. https://doi.org/10.3390/molecules31183282
Klunk MA, Caetano NR, Lorenzini G, Orbegoso EMM. Biomass-Waste-Derived Silica for Solvent-Lean Cu-SSZ-13 Porous Catalysts in NH3-SCR NOx Remediation. Molecules. 2026; 31(18):3282. https://doi.org/10.3390/molecules31183282
Chicago/Turabian StyleKlunk, Marcos Antônio, Nattan Roberto Caetano, Giulio Lorenzini, and Elder Marino Mendoza Orbegoso. 2026. "Biomass-Waste-Derived Silica for Solvent-Lean Cu-SSZ-13 Porous Catalysts in NH3-SCR NOx Remediation" Molecules 31, no. 18: 3282. https://doi.org/10.3390/molecules31183282
APA StyleKlunk, M. A., Caetano, N. R., Lorenzini, G., & Orbegoso, E. M. M. (2026). Biomass-Waste-Derived Silica for Solvent-Lean Cu-SSZ-13 Porous Catalysts in NH3-SCR NOx Remediation. Molecules, 31(18), 3282. https://doi.org/10.3390/molecules31183282

