Effects of dioxygen pressure on rates of NOx selective catalytic reduction with NH3 on Cu-CHA zeolites
Graphical abstract
Introduction
Selective catalytic reduction (SCR) with ammonia is a strategy used to abate nitrogen oxide (NOx, x = 1,2) emissions from diesel and lean-burn engines, and was implemented commercially about a decade ago with the advent of Cu-CHA zeolite catalysts that have sufficient hydrothermal stability to withstand the harsh environments encountered in automotive exhaust applications [1], [2], [3]. Typical protocols to evaluate catalysts for practical application have focused on the measurement of NOx conversion profiles as a function of temperature [4], including identifying the onset of the rapid increase in NOx conversion with increasing temperature (i.e., “light-off”) observed at low temperatures (<473 K) and the decrease in NOx conversion with increasing temperature (i.e., “seagull”-shaped dip) observed at intermediate temperatures (523–623 K) [5], [6], [7], [8]. Such macroscopic observations are manifestations of the underlying kinetic and mechanistic details of the SCR reaction on Cu-zeolites; they depend on the microscopic details of catalyst composition and active site arrangement. On Cu-CHA zeolites, these details include the number and spatial distribution of Cu cations exchanged at anionic framework sites introduced by Al substitution, and the fraction of Cu present nominally as monovalent [CuIIOH]+ (i.e., ZCuOH) and divalent CuII (i.e., Z2Cu) sites that respectively charge-compensate one and two framework Al centers [4], [9], [10], [11].
The stoichiometry of the SCR reaction using molecular oxygen as the oxidant, which is also referred to as the “standard” SCR reaction, is:Rates of “standard” SCR are typically measured at ambient pressures with NO and NH3 present in equimolar quantities (e.g., 0.03 kPa each), and O2 is present in large stoichiometric excess (e.g., 10 kPa), to resemble the concentrations present in lean-burn exhaust. The observed coexistence of both CuI and CuII species under “standard” SCR reaction conditions, and the sensitivity of their proportions to catalyst composition and structure and to the specific reaction conditions used, points to a mechanism involving a redox cycle between these two Cu states [12]. At temperatures below ~ 523 K and under SCR-relevant conditions, exchanged Cu ions in Cu-CHA zeolites are fully solvated by NH3 ligands, as evidenced by phase diagrams constructed from first-principles thermodynamic analyses of density functional theory (DFT)-based free energies of Cu-ligand complexes [9], by in situ X-ray emission spectra (XES) that show Cu-N coordination in their oxidized (CuII) and reduced (CuI) states [7], [13], and by in situ X-ray absorption near edge structure (XANES) and extended X-ray absorption fine structure (EXAFS) spectra of their oxidized and reduced states that are indistinguishable from those for four-fold and two-fold Cu-amine coordination complexes [9], [14], respectively. The coordination of Cu ions to ammonia ligands and not to zeolite framework oxygen atoms is further evidenced by the absence of second-shell Cu-T atom (T = Si, Al) scattering in EXAFS spectra collected in operando [9] and the absence of perturbed zeolite framework T-O-T vibrations in diffuse reflectance IR (DRIFTS) spectra collected in situ [15]. Thus, during low temperature NOx SCR on Cu-CHA zeolites, ammonia-solvated Cu ions are present as cationic complexes that are ionically bonded to anionic zeolite framework centers.
The preponderance of evidence is consistent with a reduction half-cycle that consumes both NO and NH3, which proceeds by NO attack on CuII-amine complexes to form nitrosamine (H2NNO)-like intermediates that decompose to yield N2, H2O, CuI-amine complexes, and an excess proton [16]. The excess proton formed upon reduction of Z2Cu sites resides on the zeolite lattice at framework oxygen adjacent to an Al site, while that formed upon reduction of ZCuOH is rejected as H2O [9]. Evidence for the reduction mechanism of mononuclear CuII-amine complexes includes DFT calculations of plausible CuII reduction pathways [9], [14], [16], [17], transient XAS [14], [16] and TPR measurements [18] that detect complete and stoichiometric reduction of CuII to CuI only when both NO and NH3 are present, and NH3 titrations that quantify the zeolitic H+ sites formed upon reduction of Z2Cu sites [9]. The details of the oxidation half-cycle are less well understood [6], [14], [19], [20], although O2 must be consumed to balance stoichiometry. The oxidation of pairs of CuI complexes with O2 is well-known in the homogeneous Cu literature [21], [22], [23]. Mononuclear CuI(NH3)2 complexes can react with O2 to form NH3-solvated binuclear CuII di-oxo complexes (e.g., (NH3)2CuII(O2)CuII(NH3)2) [6], [19], consistent with DFT calculations of plausible dual-site CuI oxidation pathways with O2 [6], [19], [24], [25] and with EXAFS spectra of Cu-CHA zeolites after their NH3-solvated CuI ions are oxidized by O2 that show second-shell Cu-Cu scattering at distances characteristic of binuclear CuII di-oxo complexes [19]. NH3-solvated binuclear CuII di-oxo complexes can be reduced to two CuI sites while consuming two equivalents of NO and NH3 to balance stoichiometry [19], via a sequence of elementary steps whose precise details have yet to be clarified.
Under low temperature “standard” SCR conditions, reaction rates on Cu-CHA (per mass or per pore volume catalyst) increase monotonically with the spatial density of isolated Cu ions (per mass or per pore volume catalyst), transitioning from a second-order dependence on Cu density in the dilute Cu limit to a first-order dependence on Cu density at higher Cu densities [9], [19], [26], [27]. In operando X-ray absorption spectra (XAS) provide direct evidence that CuI(NH3)2 is the most abundant reactive intermediate (MARI) at low Cu densities under “standard” SCR conditions [19], implying that CuI(NH3)2 oxidation with O2 is the dominant kinetically-relevant process in the kinetic regime characterized by SCR rates that show a second-order dependence on Cu density. This interpretation is consistent with transient XAS experiments performed to measure O2-assisted oxidation rates of CuI(NH3)2 complexes in Cu-CHA, which are best described by rate equations that are second-order in CuI(NH3)2 concentration [19]. Transient XAS experiments were also used to quantify the fraction of CuI(NH3)2 complexes that were oxidized by O2 in the asymptotic limit of long reaction times, and this fraction was found to increase monotonically with Cu spatial density [19]. These findings indicate that O2-assisted oxidation steps require two CuI(NH3)2 complexes, nominally isolated from one another, to co-locate within a single CHA cage to form a binuclear CuII di-oxo complex. DFT calculations indicate that transport of CuI(NH3)2 through an 8-MR window into an adjacent CHA cage that already contains a CuI(NH3)2 complex occurs with lower barriers (~35 kJ mol−1) [19] than the measured range of apparent SCR activation barriers (~40–80 kJ mol−1) [6], [14], [19], and that subsequent reaction steps to form binuclear CuII di-oxo complexes are even more facile [19], [24], [28].
Quantitative measurements that distinguish between the number of Cu sites that participate in SCR redox cycles, and the kinetics of reduction and oxidation processes catalyzed by such Cu sites, are difficult to extract from SCR rates measured under “standard” conditions that invariably convolute the kinetic contributions of both the oxidation and reduction half-cycles [12], [14], [16], [19], [29]. Here, we interrogate the catalytic function of Cu-CHA zeolites under reaction conditions perturbed far from those typical of “standard” SCR, in order to isolate either CuII reduction or CuI oxidation as the dominant kinetically-relevant process. Given that O2 is only involved as a reactant in the oxidation half-cycle, we hypothesize that dual-site CuI oxidation becomes the dominant kinetically-relevant step at dilute O2 pressures and becomes kinetically-irrelevant at higher O2 pressures. We use in operando XAS measurements to quantify the prevalent CuII and CuI fractions as a function of reaction conditions and Cu density. Apparent CuII reduction and CuI oxidation rate constants are determined from regression of rate data to an empirical model that captures the observed Langmuirian dependence of SCR rates on O2 pressure, which allows extracting kinetic parameters that describe the effects of Cu ion spatial density on SCR oxidation and reduction processes.
Section snippets
Zeolite synthesis
The parent CHA zeolites (SSZ-13, Si/Al = 15) were synthesized using previously reported procedures [9]. Briefly, a molar ratio of 1 SiO2/ 0.033 Al2O3/ 0.25 TMAdaOH/ 0.25 Na2O/ 44 H2O was used in the synthesis solution. An aqueous TMAdaOH solution (25 wt%, Sachem) was first added to deionized H2O (18.2 MΩ•cm) in a perfluoroalkoxy alkane jar (PFA, Savillex Corp.), followed by stirring the solution under ambient conditions for 0.25 h. Next, aluminum hydroxide (Al(OH)3, grade 0325, SPI Pharma) was
Both CuI oxidation and CuII reduction steps are kinetically relevant during “standard” SCR
In order to study the effects of Cu ion density on the CuI oxidation and CuII reduction processes that occur during steady-state SCR turnover, a series of Cu-CHA samples was prepared by starting with H-form zeolites of fixed framework Al content (Si/Al = 15) and performing Cu ion exchange to varying extents (Cu/Al = 0.08–0.37, Table 1; additional characterization data reported in Table S1, SI and in our prior study [19]). Cu-CHA samples are denoted as Cu-CHA-X, where X denotes the mean Cu
Conclusions
The selective catalytic reduction (SCR) of NO with NH3 on Cu-CHA zeolites is mediated by NH3-solvated CuII and CuI ions at low temperatures (<523 K), and occurs via a CuII/CuI redox cycle involving single-site CuII reduction assisted by NO and NH3 and dual-site CuI oxidation assisted by O2. When low-temperature SCR rates are measured at fixed reaction conditions (e.g., “standard” SCR conditions), they depend on the rates of both CuII reduction and CuI oxidation processes. With increasing Cu
Declaration of Competing Interest
None.
Acknowledgements
We acknowledge financial support provided by the National Science Foundation CAREER program under award number 1552517-CBET. Use of the Advanced Photon Source is supported by the U.S. Department of Energy, Office of Science, and Office of Basic Energy Sciences, under Contract no. DE-AC02-06CH11357. MRCAT operations and beamline 10-BM are supported by the Department of Energy and the MRCAT member institutions. We thank Prof. Christopher Paolucci (Virginia), Trevor M. Lardinois (Purdue), Dr. John
References (40)
Cu/Chabazite Catalysts for ‘Lean-Burn’ Vehicle Emission Control
J. Catal.
(2019)- et al.
Revisiting the Nature of Cu Sites in the Activated Cu-SSZ-13 Catalyst for SCR Reaction
Chem. Sci.
(2014) - et al.
New Insights into Cu/SSZ-13 SCR Catalyst Acidity. Part I: Nature of Acidic Sites Probed by NH3 Titration
J. Catal.
(2017) - et al.
Activation of Oxygen on (NH3CuNH3)+ in NH3-SCR over Cu-CHA
J. Catal.
(2018) - et al.
Understanding Ammonia Selective Catalytic Reduction Kinetics over Cu/SSZ-13 from Motion of the Cu Ions
J. Catal.
(2014) - et al.
Effects of Si/Al Ratio on Cu/SSZ-13 NH3-SCR Catalysts: Implications for the Active Cu Species and the Roles of Brønsted Acidity
J. Catal.
(2015) - et al.
Methods for NH3 Titration of Brønsted Acid Sites in Cu-zeolites that Catalyze the Selective Catalytic Reduction of NOx with NH3
J. Catal.
(2014) - et al.
Identification of the Active Cu Site in Standard Selective Catalytic Reduction with Ammonia on Cu-SSZ-13
J. Catal.
(2014) - et al.
A Diagnostic Test of the Kinetic Regime in a Packed Bed Reactor
Chem. Eng. Sci.
(1967) - et al.
Spectroscopic and Kinetic Responses of Cu-SSZ-13 to SO2 Exposure and Implications for NOx Selective Catalytic Reduction
Appl. Catal. A
(2019)
Transition Metal/Zeolite SCR Catalysts
WO2008132452A2,
Why Cu- and Fe-Zeolite SCR Catalysts Behave Differently At Low Temperatures
SAE Int. J. Fuels Lubr.
Selective Catalytic Reduction over Cu/SSZ-13: Linking Homo- and Heterogeneous Catalysis
J. Am. Chem. Soc.
The Cu-CHA deNOx Catalyst in Action: Temperature-Dependent NH3-Assisted Selective Catalytic Reduction Monitored by Operando XAS and XES
J. Am. Chem. Soc.
The Dynamic Nature of Cu Sites in Cu-SSZ-13 and the Origin of the Seagull NOx Conversion Profile During NH3-SCR
React. Chem. Eng.
Catalysis in a Cage: Condition-Dependent Speciation and Dynamics of Exchanged Cu Cations in SSZ-13 Zeolites
J. Am. Chem. Soc.
Characterization of Cu-exchanged SSZ-13: A Comparative FTIR, UV-Vis, and EPR study with Cu-ZSM-5 and Cu-β with Similar Si/Al and Cu/Al Ratios
Dalton Trans.
Low Absorption Vitreous Carbon Reactors for Operando XAS: A Case Study on Cu/Zeolites for Selective Catalytic Reduction of NOx by NH3
Phys. Chem. Chem. Phys.
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C. B. J. and I. K. contributed equally to this work.