1. Introduction
Tetracyclines are among the most heavily used antibiotic classes worldwide, and between 40 % and 90 % of an administered dose leaves the body still biologically active [1]. Wastewater treatment plants pass a measurable fraction to receiving waters: a synthesis of more than 170 Chinese field studies puts median antibiotic concentrations at 15 ng L−1 in treatment-plant effluent and 8.1 ng L−1 in surface water, with tetracycline among the seven compounds detected in nearly every environmental compartment [2]. Composting and conventional biological treatment remove part of the load but leave transformation products and resistance genes whose fate is poorly resolved [1], and the advanced options (oxidation, membranes and adsorption) have been reviewed for tetracycline specifically [3]. Photocatalysis is attractive here because it attacks the molecule rather than relocating it [4], and it has been demonstrated on tetracycline and on other pharmaceuticals over Nb2O5-based systems, including levofloxacin, norfloxacin and acetaminophen [5, 6, 7, 8, 9].
Nb2O5 is a useful host for this chemistry because it both binds and degrades, and because it survives repeated use [10]. Hydrothermal synthesis from an ammonium niobate complex yields a deformed orthorhombic phase that adsorbs cationic dyes by cation exchange and then mineralises them under UV [11, 12]. The same route, run for 72 h, gives a high-surface-area ortho-Nb2O5 that takes up 32 mg g−1 tetracycline at equilibrium and degrades it under UV [13], and the pairing of uptake with photolytic regeneration has since been reproduced on Nb2O5 nanofibre membranes [14] and on Nb2O5-modified clays [15]. The 3.28 eV band gap of ortho-Nb2O5 [13] restricts activation to the UV, which is why doping has become the standard lever. Metal (Zn, Mo, Bi) and non-metal (N) dopants have each been shown to shift the optical response or the defect population of Nb2O5 [16, 17, 18, 19, 20, 21], alongside the heterojunction routes that dominate the recent literature [22]. Cerium is a natural candidate because the Ce3+/Ce4+ couple supplies oxygen vacancies that act as charge traps [23, 24], and the reciprocal composition, Nb-doped CeO2, degrades tetracycline about twice as fast as undoped CeO2 [25]. Ceria is itself a common doping host [26, 27]; Ce added to Nb2O5 is the arrangement examined here.
What these studies share is the metric. Performance is reported as the fraction of pollutant lost from solution after a fixed irradiation time, occasionally with an apparent rate constant attached [5, 17, 28]. On a material that adsorbs strongly the metric is ambiguous by construction, because two mechanisms with different consequences, transfer to a surface and transformation under illumination, are summed into one number [14]. The ambiguity matters for doping series in particular: a dopant that raises surface affinity and a dopant that raises photochemical activity both move the same percentage upward, and ranking a series by that percentage cannot tell which happened. Studies that do separate the stages usually do so to subtract adsorption as a nuisance term before fitting kinetics. To our knowledge, no doped or metal-loaded Nb2O5 series has reported dark-stage uptake and UV-stage removal as a paired property of each composition, and that is the gap this work addresses.
Herein we resolve removal into its dark and UV stages for a Ce-loaded niobium oxide series by following the solution in-line through a dark stage and an illuminated stage, and by renormalising every trace to its own measured initial concentration. UV-C is used deliberately: the question is how removal divides between the stages, not how far the response extends into the visible. The three compositions turn out not to differ significantly in total removal but to differ clearly in how that total is split, with dark uptake and the apparent UV-stage rate constant moving in opposite directions across the series.
2. Materials and Methods
1 summarises the synthesis and the reactor.
2.1 Synthesis
Ammonium niobate(V) oxalate hydrate (2.244 g) was dissolved in 70 mL deionised water under magnetic stirring at 200 rpm and room temperature. Cerium(III) nitrate hexahydrate was then added at nominal Ce loadings of 1, 3 and 5 mol % relative to Nb, and the solution was stirred to homogeneity. Each solution was transferred to a 100 mL polytetrafluoroethylene (PTFE)-lined autoclave and held at 175 °C for 72 h. The solid was recovered by vacuum filtration, dried at 80 °C for 4 h, ground in an agate mortar and stored in sealed glass vials. The three products are denoted Ce1%–Nb2O5, Ce3%–Nb2O5 and Ce5%–Nb2O5. The Ce content of the products was not determined, so the loadings are nominal throughout. The niobium precursor, temperature and duration reproduce the route reported for undoped ortho-Nb2O5 [12, 13], so that, apart from the added cerium nitrate, the synthesis matches that benchmark; no undoped material was prepared in this campaign.
2.2 Characterisation
X-ray diffraction (XRD) patterns were collected over 5 °–80 °
2.3 Removal Experiments
A 500 mg L−1 tetracycline hydrochloride stock was
prepared in deionised water and diluted to working concentrations
with no buffer or background electrolyte, so the ionic strength is
set by the salt alone, about 4 × 10−5 mol L−1
at 20 mg L−1. Solution pH was neither adjusted nor
recorded. Tetracycline has p
Runs were carried out in the closed photoreactor described in
[26, 25], fitted here with
a single 10 W Philips TUV UV-C lamp (
Two experiments were run, both with 0.05 g solid in 200 mL
solution. Each condition was run in duplicate as two independent
runs, each with fresh solid and freshly diluted solution; values are
the mean of the two runs. The
2.4 Data Treatment
Absorbances were converted to concentrations through the
calibration line
Removal was decomposed into the two stages of the contact-time run,
3. Results and Discussion
3.1 Structure and Surface Groups
All three patterns (2a) carry the same reflection set: a sharp line at 22.6 °, weaker lines at 46.2 ° and 54.8 °, a broad hump centred near 26.5 °, and a pair of narrow lines at 16.15 ° and 16.67 °. The 22.6 ° and 46.2 ° reflections are those of the deformed orthorhombic phase obtained by this route [12, 35]. The low-angle pair is not part of that pattern and is markedly narrower than it (full widths of 0.31 °–0.36 ° against 0.62 °–0.66 ° at 22.6 °), so it belongs to a second, better-ordered phase, plausibly an ammonium-bearing layered niobate carried through from the precursor [11]. We do not assign it further here; a database search-match on the full pattern, including an undoped reference, is needed for that. Apparent crystallite sizes from the 22.6 ° width [36], uncorrected for instrumental broadening, are 12.3 nm, 12.5 nm, & 13.1 nm for Ce1%–Nb2O5, Ce3%–Nb2O5 and Ce5%–Nb2O5.
What changes across the series is the balance between the two phases, and it changes only at the top loading. Ce1%–Nb2O5 and Ce3%–Nb2O5 are indistinguishable: the intensity of the 16.15 ° line relative to the 22.6 ° niobate reflection is 0.63 and 0.61, and the ratio within the low-angle pair is 0.88 and 0.87. In Ce5%–Nb2O5 the same ratios are 1.71 and 1.32, a 2.7-fold growth of the low-angle phase against the niobate, while the integrated intensity over 10 °–60 ° falls by 44 % relative to Ce1%–Nb2O5. At 5 % nominal loading, Ce is therefore not accommodated without changing the product: it shifts the product towards the secondary phase and costs long-range order, consistent with the disorder reported for heavily doped Nb2O5 and for the reciprocal Nb–CeO2 system [37, 25]. No reflection appears at 28.5 °, 33.1 ° or 47.5 °, so segregated fluorite CeO2 is below the detection limit in all three samples.
Infrared spectra (2b) show the Nb–O and Nb–O–Nb envelope at 480 cm and 560 cm, a band at 1415 cm–1420 cm assigned to the ammonium deformation, the water bending mode near 1640 cm, and a broad hydroxyl stretch centred between 3235 cm and 3363 cm; the sharp feature at 2350 cm is atmospheric CO2. Retained ammonium appears in the undoped reference spectrum as well, which supports the cation-exchange picture established for this material [12] but does not by itself discriminate between the three Ce loadings.
Electron microscopy (3)
shows the same texture in all three samples: irregular agglomerates
built from sub-micrometre primary particles, with no faceted
crystals resolved at 10000
3.2 Removal Traces and the Two Stages
4a shows the full 180 min traces. Removal rises steeply for the first 15 min in the dark, flattens towards 60 min, and then climbs again under illumination to the end of the run. The first illuminated reading, at 75 min, lies below the 60 min value in four of the six runs, by 0.2–2.1 and most clearly on Ce3%–Nb2O5 (1.4 , & 2.1 ), and above it by 0.2–0.6 in the other two. We read this dip as a change in the measured absorbance rather than as a pause in removal: tetracycline photolysis intermediates absorb in the same region as the parent compound, so a single-wavelength reading cannot separate parent loss from the appearance of absorbing products (3.5).
| Sample |
|
|
|
|
|---|---|---|---|---|
| Ce1%–Nb2O5 | 24.4 |
16.8 |
53.5 |
3.52 |
| Ce3%–Nb2O5 | 36.6 |
9.2 |
57.1 |
2.30 |
| Ce5%–Nb2O5 | 27.5 |
15.7 |
54.2 |
3.33 |
The totals do not separate the materials. End-of-run removal
spans 53.5 %–57.1 % (1), a
range of 3.7 against a replicate standard deviation of up to 3.2
(Ce5%–Nb2O5, whose two runs differ by 4.5); no
pairwise comparison approaches significance (Welch
Dark uptake does separate them, and the UV stage moves the
opposite way (5). Dark
uptake is 24.4 ± 0.7 mg g−1 for
Ce1%–Nb2O5, 36.6 ± 0.8 mg g−1 for
Ce3%–Nb2O5 and 27.5 ± 0.4 mg g−1
for Ce5%–Nb2O5; every pair is separated
(
The campaign has no photolysis blank
(3.5), so the UV-stage
numbers include direct photolysis of tetracycline at 254 nm
[38, 39]. That term cannot,
however, produce the spread between compositions. All six runs used
the same lamp, reactor geometry, volume and solid mass, so direct
photolysis can differ between runs only through the absorbance of
the solution and through any effect of the solids on the light or
the solution. Its pseudo-first-order constant can only stay level or
fall as the solution absorbs more of the light, which would make the
runs with the lowest
The normalisation of
For an external reference point, undoped ortho-Nb2O5 from the same synthesis route takes up 32 mg g−1 tetracycline at equilibrium [13]. The Ce3%–Nb2O5 value of 36.6 mg g−1 is reached in 60 min at a single initial concentration, so the two numbers are not measured on the same basis and the comparison is indicative only, and the undoped material is a benchmark, not a control. It does indicate that the Ce-loaded materials are in the same capacity band as the undoped host rather than an order apart.
3.3 Kinetic Models and Their Residuals
Both models that dominate the adsorption literature reproduce the
dark stage (4b): pseudo-first
and pseudo-second order return
The illuminated stage behaves the same way
(4c). First and zero order
are indistinguishable (
The residuals are more informative than the ranking. In the dark stage (4e) the pseudo-first-order residuals are largest at 5 min and 15 min, spanning −3.9 mg g−1–2.5 mg g−1, and their sign there differs between runs: the misfit is concentrated in the steep first quarter of the stage. In the illuminated stage (4f) they are not scattered but ordered in time: negative at 60 min, positive through 75 min–90 min, then decaying towards zero. Random error does not produce that shape. It is the absorbance excursion that follows lamp-on (3.2), and it sets a floor on how far any rate constant taken from this window can be pushed.
3.4 Initial Concentration
|
|
|
|
|
plateau slope ( min−1) |
|---|---|---|---|---|
| 10.1 | 21.7 |
8.8 |
0.123 |
0.06 |
| 15.0 | 32.3 |
19.4 |
0.222 |
0.17 |
| 19.7 | 33.9 |
26.8 |
0.270 |
0.20 |
| 24.6 | 41.5 |
40.9 |
0.419 |
0.21 |
Fractional removal after 60 min rises with initial concentration, from 21.7 % at 10.1 mg L−1 to 41.5 % at 24.6 mg L−1 (2). Read as a performance statement, as removal efficiency against initial concentration routinely is [5, 6, 28], this is anomalous, since a system limited by a fixed flux of reactive species loses a smaller fraction of a larger load.
The time traces show that it is an artefact of the fixed window
(6a). At
10.1 mg L−1 the trace is flat over the last quarter of
the run, 0.06 ± 0.09 min−1, so the system has stopped
changing; at 24.6 mg L−1 it is still rising at
0.21 ± 0.03 min−1 when the run is stopped. A 60 min
percentage therefore compares a system that has reached its plateau
against one that has not, and the comparison rewards the latter. On
a mass basis the picture is straightforward
(6b): specific removal
climbs from 8.8 mg g−1 to 40.9 mg g−1 over the
same range with no sign of saturation, and the initial rate rises
roughly in proportion to the load, from 0.123 mg L min−−1
to 0.419 mg L min−−1 (
One condition was run twice, once in each experiment, and the two do not agree. At 20 mg L−1 with Ce3%–Nb2O5, removal after 60 min was 45.7 % when the stage was dark and 33.9 % when the lamp was on from the start (6c), on measured initial concentrations differing by 0.3 mg L−1. The gap of 11.7 opens inside the first 5 min, where the two runs stand at 21.1 % and 7.9 %. Illumination did not add to removal over this window; it appeared to subtract from it. Three readings survive the data: photolysis intermediates absorbing at the analytical wavelength, so that part of the parent loss is masked (3.2); desorption as the lamp warms a closed reactor; and ordinary between-campaign variability, the two experiments having been run separately. Nothing here separates them, and the gap is large enough that results from the two experiments should not be pooled.
3.5 What These Data Cannot Establish
The campaign carries no undoped control, no photolysis blank and no dark control extended to 180 min. Without them the series cannot be used to claim that Ce loading improves on ortho-Nb2O5. Undoped material from the same route takes up 32 mg g−1 tetracycline and has a Brunauer–Emmett–Teller (BET) area of 242 m2 g−1 [13], but it was tested under a separate protocol and serves as a benchmark, not a control. The UV-stage numbers include whatever direct 254 nm photolysis contributes; at that wavelength tetracyclines absorb and photolyse without any catalyst [38, 39], so in absolute terms the contribution is not negligible. 3.2 shows only that it cannot account for the differences between compositions. All comparisons above are therefore internal to the Ce series, where the missing controls would act alike on the three compositions and, for photolysis, cannot produce the differences between them.
The Ce loadings are nominal. Neither the Ce content of the products, nor its distribution, nor its oxidation state was measured, so the series is defined by what entered the autoclave rather than by what is in the solid. The growth of the low-angle phase at 5 % Ce (3.1) shows that Ce changes the product, and the absence of fluorite reflections excludes segregated CeO2 above the diffraction detection limit; neither establishes substitution into the Nb2O5 lattice. For that reason we describe the materials as Ce-loaded rather than Ce-doped.
Detection is by absorbance at a single wavelength, 273 nm. That measures the disappearance of the parent chromophore, not degradation or mineralisation; under UV alone, oxytetracycline loses most of its parent signal while about 7 % of its carbon is mineralised over the same hour [46]. The reading is also open to interference from transformation products that absorb near the parent maximum, which would make UV-stage removal appear smaller than it is, and from changes in absorbance on lamp-on, visible as the post-illumination dip of 4a. Scattering by the catalyst does not enter the reading, because the solution was filtered before the flow cell. For these reasons we report UV-stage removal of the parent signal and do not describe it as degradation. Total organic carbon or chromatographic detection would settle these points.
Solution conditions were controlled only loosely. pH and temperature were not recorded, the lamp shares the closed box with the reactor, and the solution carries no background electrolyte. The electrostatic state of the surface and of tetracycline during the runs is therefore unknown, and the uptake ranking cannot be linked to it.
The mechanism behind the uptake maximum at 3 % Ce remains open. Diffraction and infrared spectroscopy resolve a structural difference between Ce5%–Nb2O5 and the other two, but Ce1%–Nb2O5 and Ce3%–Nb2O5 are indistinguishable by both techniques although Ce3%–Nb2O5 takes up 50 % more in the dark. Surface area, pore volume, pore-size distribution, zeta potential, point of zero charge and Ce oxidation state were not measured, and one of those is the likely explanatory variable.
The two experiments are also not on a common baseline, as 6c shows at the single condition they share; only 3.2 and 3.3, which draw on one experiment, are internally consistent.
Finally, each condition was run in duplicate. The dark-uptake
separation is large relative to that spread, but the
4. Conclusions
Ce loading between 1 % and 5 % did not measurably change how much tetracycline a hydrothermal niobium oxide removes in 180 min; it changed which stage does the removing. Dark uptake peaks sharply at 3 % Ce, at 36.6 ± 0.8 mg g−1 against 24.4 ± 0.7 mg g−1 at 1 %, while the apparent UV-stage rate constant moves the opposite way and the two anticorrelate across individual runs. End-of-run removal spans only 3.7 across the series and separates nothing.
Two practical consequences follow. A loading or doping series of an
adsorbent tested under illumination cannot be ranked by fixed-time
removal, because the metric sums the two stages it should be
distinguishing; recording