Electrochemistry Application — Dual single atomic Fe-Ni sites in N‑doped nanoporous carbon for high-efficiency potassium periodate activation toward pollutant abatement

Measurement evidence

Electrochemistry Application

Dual single atomic Fe-Ni sites in N‑doped nanoporous carbon for high-efficiency potassium periodate activation toward pollutant abatement · Yao Y., Ma Z., Ma Z. et al. · Separation and Purification Technology · 2025 · 128091

6 measurement groups · 25 results

Reported values remain attached to the sample, method, conditions, extraction quality and source location that produced them.

Chemical oxygen demand (COD)

Fe2Ni1-NC-900 · Powder

COD determined by HACH digestion instrument and UV-vis spectrophotometer after Fe2Ni1-NC-900/PI oxidation.

Geometry
aqueous treated solution
Context
MOF-derived catalyst powder in PI system
Measurement source
10; SI 9 · 3.7 Evolution mechanism · Figure S8
PropertyReported valueNormalised valueUncertaintyOrigin and qualitySource
COD removal efficiency52.3 %52.3 %Text
Exact Reported
10 · 3.7 · Figure S8

Recycling and regeneration catalytic tests

Used Fe2Ni1-NC-900 · Powder

Recovered catalyst washed with ethanol and water, dried at 60 deg C, reused; annealing regeneration at 900 deg C in N2 for 2 h.

Temperature
298
Atmosphere
reaction in water; annealing in N2
Geometry
batch reactor
Context
used and regenerated MOF-derived catalyst powder
Measurement source
4; 7-8 · 2.2; 3.4 · Figure 4e
PropertyReported valueNormalised valueUncertaintyOrigin and qualitySource
Orange II removal after annealing regeneration89 % after annealing treatment89 %Text
Rounded Reported
8 · 3.4 · Figure 4e
Orange II removal after three repetitionsdecreased from 100.0 % to 62.0 % after three repetitions62 %Text
Exact Reported
7-8 · 3.4 · Figure 4e

Continuous-flow fixed-bed oxidation

Fe2Ni1-NC-900 · Powder

Continuous fixed-bed apparatus with 0.5 g Fe2Ni1-NC-900; Orange II inflow concentration 50 mg/L.

Geometry
continuous fixed-bed apparatus
Context
MOF-derived catalyst powder packed for continuous flow
Measurement source
7-8 · 3.4 Durability and practical application · Figure 4f
PropertyReported valueNormalised valueUncertaintyOrigin and qualitySource
Continuous-flow removal efficiencyMarked as a best value within this paper100 % removal efficiency100 %Text
Exact Reported
8 · 3.4 · Figure 4f
Orange II-contaminated water treated in continuous flow8 L8 LText
Exact Reported
8 · 3.4 · Figure 4f

Batch catalytic oxidation of Orange II by periodate activation

Fe2Ni1-NC-900 · Powder

200 mL reactor with 300 rpm stirring, 25 +/- 1 deg C; standard Figure 3 parameters: catalyst 0.05 g/L, PI 0.05 g/L, organic 30 mg/L, no pH adjustment.

Temperature
298
Geometry
batch reactor
Context
MOF-derived catalyst powder in aqueous pollutant oxidation
Measurement source
2-3; 5-6 · 2.2; 3.2 · Figure 3
PropertyReported valueNormalised valueUncertaintyOrigin and qualitySource
Orange II elimination by Fe2Ni1-NC-900 adsorption only41.3 % within 50 min after adding Fe2Ni1-NC-90041.3 %approximatelyText
Approximate
5 · 3.2 · Figure S3a
Orange II removal by Fe1Ni1-NC-900/PI93 %93 %Text
Rounded Reported
5 · 3.2 · Figure 3c
Orange II removal by Fe1Ni2-NC-900/PI82 %82 %Text
Rounded Reported
5 · 3.2 · Figure 3c
Orange II removal by Fe2Ni1-NC-1000/PI91 %91 %Text
Rounded Reported
5-6 · 3.2 · Figure 3d
Orange II removal by Fe2Ni1-NC-800/PI65 %65 %Text
Rounded Reported
5-6 · 3.2 · Figure 3d
Orange II removal by Fe2Ni1-NC-900/PIMarked as a best value within this paper100.0 %100 %Text
Exact Reported
5-6 · 3.2 · Figure 3d
Orange II removal by Fe2Ni1-NC-950/PI86 %86 %Text
Rounded Reported
5-6 · 3.2 · Figure 3d
Orange II oxidation by Fe2Ni1-NC-900/PIMarked as a best value within this papercompletely oxidized in 50 min100 %Text
Rounded Reported
5 · 3.2 · Figure 3a
Orange II removal by Fe4Ni1-NC-900/PI84 %84 %Text
Rounded Reported
5 · 3.2 · Figure 3c
Orange II removal by Fe-NC-900/PI91 %91 %Text
Rounded Reported
5 · 3.2 · Figure 3c
Orange II removal by NC-900/PI28 %28 %Text
Rounded Reported
5 · 3.2 · Figure 3c
Orange II removal by Ni-NC-900/PI43 %43 %Text
Rounded Reported
5 · 3.2 · Figure 3c

Radical scavenging and EPR spectroscopy

Fe2Ni1-NC-900 · Powder

TBA, MeOH, EtOH, p-BQ, L-histidine and DMSO scavengers; EPR with DMPO for radicals and TEMP for singlet oxygen.

Temperature
298
Atmosphere
air or N2-saturated tests as noted
Geometry
aqueous catalytic reaction
Context
MOF-derived catalyst powder
Measurement source
3; 8-9 · 2.2; 3.5 · Figure 5; Figure S6
PropertyReported valueNormalised valueUncertaintyOrigin and qualitySource
DMSO high-valent Fe/Ni-oxo scavenging result0.01 mM DMSO did not reduce Orange II removal efficiency0.01 mMText
Exact Reported
9 · 3.5 · Figure 5a
Orange II degradation with excess L-histidineremained at 45 %45 %Text
Rounded Reported
9 · 3.5 · Figure S6e
Orange II degradation with 0.5 mM L-histidinedecreased from 100 % to 51 %51 %Text
Rounded Reported
9 · 3.5 · Figure S6e
TEMP-EPR evidence for singlet oxygencharacteristic three-peak signal (1:1:1) appeared when Fe2Ni1-NC-900 and PI were added togetherQualitative
Qualitative
9 · 3.5 · Figure 5d

Zeta potential and pH-dependent oxidation

Fe2Ni1-NC-900 · Powder

Malvern Zetasizer Nano ZS90 for zeta potential; Orange II oxidation measured at initial pH 2.03-9.01.

Temperature
298
Geometry
aqueous dispersion
Context
MOF-derived catalyst powder
Measurement source
6-7 · 3.3 Influencing factors · Figure 4a-b
PropertyReported valueNormalised valueUncertaintyOrigin and qualitySource
Orange II oxidation efficiency in 5.0 mM carbonate64.0 %64 %Text
Exact Reported
7 · 3.3 · Figure 4c
Isoelectric point pHpzc of Fe2Ni1-NC-900about 2.532.53 pHaboutText
Approximate
6 · 3.3 · Figure 4b
Orange II removal in river water68 % Orange II elimination68 %Text
Rounded Reported
7 · 3.3 · Figure 4d
Orange II removal in tap water89 % removal efficiency within 50 min89 %Text
Rounded Reported
7 · 3.3 · Figure 4d