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Supplementary Material
Nitrate reduction on surface of Pd/Sn catalysts
supported by coal fly ash-derived zeolites
Jaehyeong Parka, Yuhoon Hwangb, and Sungjun Baea,*
aDepartment of Civil and Environmental Engineering, Konkuk University, 120 Neungdong-
ro, Gwangjin-gu, Seoul 05029, Republic of Korea
bDepartment of Environmental Engineering, Seoul National University of Science and
Technology, 232 Gongneung-ro, Nowon-gu, Seoul 01811, Republic of Korea
*Corresponding author: [email protected]
phone: +82-42-450-3904
Journal of Hazardous Materials
Chemicals
Supplementary Material
Acetic acid (99.7 %, Dae Jung Chemical, Korea) and NaOH (97.0 %, Dae Jung Chemical,
Korea) were used for the pretreatment of NMFA surface and the alkaline fusion of NMFA,
respectively. Precursor solutions of Pd and Sn were prepared with PdCl2 (99%, Sigma-
Aldrich, USA) and SnCl4 (99%, Sigma-Aldrich, USA). To prepare Pd/Sn catalysts supported
by other support materials, silicon dioxide (~99%, 0.5-10 μm, Sigma-Aldrich, USA) and
aluminum oxide (99.5%, ≤10 μm, Sigma-Aldrich, USA) were used. Sodium borohydride
(98%, Sigma-Aldrich, USA) was used to activate Pd-Sn bimetallic catalysts. Potassium
nitrate (99.0%, Duksan Pure Chemical Co., Korea) and ammonium chloride (98.5%, Duksan
Pure Chemical Co., Korea) were used for stock and standard solutions for ion
chromatography (IC). Sodium bicarbonate (99.7%, Sigma-Aldrich Inc., USA), sodium
carbonate (99.95%, Sigma-Aldrich Inc., USA), sulfuric acid (60%, Dae Jung Chemical,
Korea), and methanesurfonic acid (Sigma-Aldrich Inc., USA) were used to prepare eluent for
IC operation.
Preparation of NMFA
An exact amount of CFA (50.0 g) was washed with 500 mL of DIW under mechanically
stirring at 500 rpm for 1 h. A neodymium magnet was put in the CFA suspension under
vigorous stirring (500 rpm), and black particles attached on the magnet were removed. This
procedure was repeated until the iron-rich FA particles were completely removed from the
suspension. The remaining particles (i.e., NMFA) were washed with DIW three times by
centrifugation (7000 rpm, 3 min) and oven-dried at 105 °C for 24 h. Then, NMFA was
further treated with acetic acid to remove impurities on the surface. An exact amount of
NMFA (20.0 g) was transferred into a beaker containing 200.0 mL of 5 M acetic acid
solution, and then the mixture was magnetically stirred at 700 rpm for 2 h. Then, the mixture
was centrifuged for the solid-liquid separation. The supernatant was removed, and the
Supplementary Material
remaining NMFA particles were washed with DIW three times by centrifugation (7000 rpm,
3 min) and oven-dried at 105 °C for 24 h.
Characterization of CFA-derived zeolites and catalysts
The mineral phases of raw CFA and all FA-derived zeolites were identified by XRD analysis
(Bruker DE/D8 Advance, Germany). The prepared samples were scanned from 0° to 90° 2θ
with a scan speed of 2° min-1. Specific surface areas of the samples (Zeolite-X&A9, Zeolite-
X&A&HS12, Zeolite-X&HS15, Zeolite-X&HS18, and Pd-Sn/Zeolite-X&HS15) were
measured by nitrogen adsorption and desorption at -196 ◦C with BET surface analyzer
(3Flex, Micromeritics, USA) to investigate the effect of crystallization time on the surface
area of zeolites. The morphological characteristic of zeolites and dispersion of Pd-Sn/Zeolite-
X&HS15 was investigated using HR-FESEM (SU8010, Hitachi High Technologies
Corporations) equipped with an energy-dispersive X-ray spectroscopy (EDS). The oxidation
states of Pd and Sn on the zeolite surface was investigated by the XPS analysis using Sigma
Probe system (Thermo Scientific, USA) with Al K X-ray (1486.7 eV) radiation with a
source power of 75 W. The surface charging effects were corrected using the C 1s peak at
285 eV as a reference. The narrow-scan spectra obtained in the ranges 350–330 eV, and 502–
480 eV were used to identify oxidation states of Pd and Sn species on the Pd-Sn/Zeolite-
X&HS15 surface, respectively.
For surface analysis of Pd-Sn/Zeolite-X&HS15, the catalyst after activation with NaBH4
was transferred to an anaerobic chamber (Coylab) and washed with deaerated deionized
water (DDIW), DDIW + deaerated ethanol (v:v=1:1), and deaerated ethanol sequentially. We
also analyzed Pd-Sn/Zeolite-X&HS15 after the NO3− reduction (90 min-reaction) to
investigate the stability of catalyst in this study. After finishing the reaction, the suspension
was purged with Ar and then the catalyst was collected through vacuum filtering using a
Supplementary Material
membrane filter (0.2 μm, Advantech, Japan) in anaerobic chamber to minimize the surface
oxidation by O2 in air. The collected catalyst was washed with DDIW, DDIW + deaerated
ethanol (v:v=1:1), and deaerated ethanol sequentially.
Analytical methods
To measure the concentrations of NO3−, nitrite (NO2
−), and ammonium (NH4+), 3 mL of
sample was taken from the reactor using a 5 mL syringe (Korea Vaccine Corp., Korea) at
each sampling time. The sample was immediately filtered using 2 μm PVDF syringe filter
(Whatman) and the concentration of NO3− and NO2
− in the filtrate was determined using ion
chromatography (IC) (Metrohm, 883 Basic IC plus) equipped with a compact autosampler
(Metrohm, 863 Compact IC) and anion column (Shodex IC Anion Sep No.82504A). Mixture
of Na2CO3 (3.5 mM) and NaHCO3 (3.5 mM) was prepared for IC eluent. The concentration
of NH4+ was measured using IC (DIONEX, ICS-2000) equipped with an autosampler
(DIONEX, AS40 automated sampler) and cation column (DIONEX, No.046073).
Table S1. Nitrate removal, kinetics and N2 selectivities of bimetallic catalysts for nitrate reduction
Catalyst NO3− removal (%)
N2 selectivity (%)
K (min-1) K’ (min−1
gcat−1)
K’’ (L min-1
gPd−1)
Pd/Sn/zeolite-X&A9
99.23± 0.23 87.34±0.07 0.032±0.001 0.130±0.002 1.728±0.028
Pd/Sn/zeolite- 100 87.29±0.00 0.041±0.001 0.164±0.005 2.181±0.069
Supplementary Material
X&A&HS12Pd/Sn/zeolite-
X&HS15100 88.06±0.19 0.055±0.005 0.219±0.021 2.922±0.276
Pd/Sn/zeolite-X&HS18
100 86.88±0.17 0.050±0.003 0.201±0.013 2.673±0.169
Table S2. Surface area, pore volume, and pore size of each synthesized zeolite samples. Synthesized zeolites BET surface area
(m2 g-1)Pore volumea (cm3 g-1)
Zeolite-X&A9 62.95 0.089
Zeolite-X&A&HS12 97.00 0.101
Zeolite-X&HS15 94.82 0.112
Zeolite-X&HS18 70.15 0.091
aBJH Adsorption cumulative volume of pores between 1.000 Å and 3000.000 Å diameter.
Supplementary Material
Figure S1. XRD patterns of of (a) CFA, Zeolite-X&A9, -X&A&HS12, -X&HS15, and -
X&HS18. XRD peaks of (b-d) hydroxy sodalite (2θ = 14.0°, 24.4°, and 34.8°) and (e-g) Na-
X (2θ = 15.4, 23.3 and 26.7°).
Supplementary Material
Figure S2. HR-FESEM images of Zeolite-X&A9 (a, a1), -X&A&HS12 (b, b1), -X&HS15 (c,
c1), and -X&HS18 (d, d1).
Supplementary Material
Figure S3. EDS analysis of Zeolite-X&A9 (a), -X&A&HS12 (b), -X&HS15 (c), and -
X&HS18 (d); EDS electron mapping of O (a1, b1, c1, d1), Al (a2, b2, c2, d2), and Si (a3, b3,
c3, d3).
Supplementary Material
Figure S4. The concentrations of NO3−, NO2
− and NH4+ as a function of reaction time during
the catalytic reduction of NO3− on Pd-Sn/Zeolite-X&HS15 catalysts (1.25 g/L, Pd=1.5 wt.%,
Sn=1.5 wt%) with only H2 , only CO2, and both H2 and CO2; H2 flow rate = 30 cc/min, CO2
flow rate = 40 cc/min. Reaction time was 90 min.