Overview
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Key numbers
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- oxides,5,24 carbon nanotubes,5,24,25 and nanoparticles ically and chemically stable under adsorption test conditions.
- considered. In this framework, iron oxide NPs can be grown removal from 15% w/w iron oxide-based mesostructured (15Fe-
- stable at acidic pH, and preventing the leaking and the aggre- inuence in batch tests. The iron oxide-SBA-15 composite has
- in composites with TiO2,50 CoFe2O4,36 MnO2,37 CuO,38 and Pluronic 123 (P123), hydrochloric acid (37% w/w), sodium
- Fe2O3.39 Mesostructured silica has also been applied for water acetate (NaAc, 99% w/w), sodium sulfate (99.2% w/w), and
- remediation with several organic functional groups, especially toluene (99.7% w/w) were purchased from VWR International
- thiol40–43 and amino functionalities,44–49 revealing high perfor- S.r.l. Acetic acid (HAc, 99.8% w/w) and tetraethyl orthosilicate
- mance and easy regeneration. In addition, macroporous silica (TEOS, 98% w/w) were purchased from Aldrich. 3-Amino-
- (macroporous ordered siliceous foams, MOSF)51–61 has been propyltriethoxysilane (APTES, 97%), ethanol (96% w/w), iron(III)
- used as a support, sometimes coupled with mesopores.62,63 The nitrate nonahydrate (98% w/w), and n-hexane (97% w/w) were
- ingoing water as a potential column material. Indeed, despite ments, arsenic(V) standard solution (10 000 mg mL1 As in 10%
- blockage and uneven distribution within the pores, affecting ppb, specic resistance of 0.741 mS cm1) was used.
- 1.65 mL of APTES (97%) was added to the mixture and stirred at
- a 15 mL test tube together with 2 mL of nitric acid 20% w/w, and
- The plotted data qt vs. Ct was then tted by the pseudo-rst using a PerkinElmer STA 6000, in the range 25–850 C, with
- the adsorption data in the p/p0 range 0.05–0.17.31 Total pore
- where K0 and K00 are the psuedo-1st order and pseudo-2nd order volume was calculated at p/p0 ¼ 0.875, while mean pore diam-
- (4 mL) 4 mL of water and 1 mL of a 20% w/w nitric acid was NaOH to modify the pH from 2 to 9. The scattering cell
- spheroidal particles with sizes in the 150–1000 nm range are
- based circularity factor of around 0.5 for both samples (Table
- of SBA15 is conrmed by the distinct step in the range 0.6–0.8 p/ Fe2O3 NPs in the two most common crystalline phases, hema-
- Table 1 Surface area (SBET), pore volume (PV), calculated pore diameter by density functional theory (DFT) fit method (Dp (DFT)) and Barrett–
- composites, an attempt was carried out taking into account the walls were not affected (Table 1). The presence of a bimodal
- is the primary phase (60–70%), and both phases are in the form SBA15 can be justied due to the presence of small NPs instead
- matrix, as evidenced by TEM. The presence of maghemite is also to 219 m2 g1 (Fig. 1d and Table 1).
- HRTEM image reported in Fig. S8.†72,73,86–88 SE-SEM (Fig. S4†) and image analyses (Fig. S5 and Table S1†)
- primary component (70–80%), as conrmed by the tentative and MOSF aer the deposition of Fe2O3 are shown in Fig. 3a and
- Table S2†). The results suggest for both samples, the presence The honeycomb architecture of the macropores of the MOSF
- content in the nal sorbent is 15% w/w, as assured by the
- component (60–80%) in the form of very small NPs (3–6 nm),
- Table S4 and Fig. S11†) revealed a higher adsorption capacity at Radushkevich models are not suitable, while the best tting is
- probably as a consequence of the interplay of more reactive SBA15 (0.96 instead of 0.98) samples, meaning that more than
- literature, the effect of the size of NPs on the As(V) adsorption for rst points in Fig. 5 in all experimental curves (range of Ce
- CHN analyses permitted us to evaluate 2.5% of NH2 groups and Among the tested adsorbents, better performances for the
- water, while the second one, of about 10% weight loss and also other authors have reported a qm act (qm of the active phase)
- z3450 cm1, H–O–H bending mode at z1630 cm1), and the that mesostructured materials are more suitable to disperse
- range (pH 3–9), as indicated by the zeta potential vs. pH the APTES groups. Indeed, for the iron oxide modied silica,
- in Table S5† (Fig. S15† for the corresponding pH values). The SBA15 and APTES-SBA15 sorbents in the contact time range
- data were tted by different isotherm models, as indicated in 10–1140 min (initial As(V) concentration 10 mg L1) (Table S6†).
- the experimental section (Table 2): Langmuir (eqn (2)), The qt vs. t plots (Fig. 6a) were tted with the pseudo 1st and 2nd
- testing only 40% of arsenic is removed. The pseudo 1st order increasing initial arsenic concentration. This behavior suggests
- (ki) of almost one order of magnitude higher (Table 3). and under all adsorption conditions (from 23 to 107 mg L1)
Methods (brief)
- as the most promising sample for As(V)-removal. The amino-functionalized SBA15 adsorbent (3-
- adsorbent platform. Nevertheless, the role of the different Synthesis of SBA-15. The SBA-15 sample was synthesized
- Synthesis of MOSF. The MOSF sample was synthesized ðC0 Ce ÞV
- work.72,73 2.0 g of dried silica sample (120 C for 48 h in air) was In the Freundlich isotherm model (eqn (3)), KF is the
- analyzed by ICP-OES. The model is used to differentiate between physisorption
- ðC0 Ct ÞV ethanol dispersion of the sample on a 200-mesh carbon-coated
- Autosorb iQ MP from Quantachrome Instruments. The samples
- t 1 t from Malvern. An 8 mm3 sample was applied to a glass plate
- qt K qe2 qe2 with the sample dispersion unit (SDU) with low energy. The
- Germany). For this purpose, the samples were xed with
- double-sided adhesive carbon tape on an aluminum pin sample
- optical emission spectrometry (ICP-OES) using an iCAP 7400 were carried out with an acceleration voltage of 6 keV at
- (1 mg L1), Fe (1 mg L1); standard 7: As (0.5 mg L1); standard the data. The sample was prepared by suspending the
- 8: As (0.1 mg L1); standard 9: As (0.05 mg L1). To each sample composites (5 mg mL1) in distilled water and adding HCl and
- The sorbent samples were characterized by small-angle and
- structure COD ID used for the renement is 1 010 369.84 Wall TEM, and SEM. The SA-XRD patterns of the bare SBA15 sample
- contrary, the bare MOSF sample featured a type II isotherm
- SBA15, and about 150 mm for the MOSF sample, with a number-
Implications
This page makes the source discoverable for category-level evidence routing. Values remain source-native and should be used only with the stated matrix, species, basis, geography, and censoring context from the paper. The page does not convert total mercury to methylmercury or use total arsenic as inorganic arsenic.
Wiki pages this source may touch
- Fish — marine, predatory (tuna, swordfish, shark, king mackerel)
- Fish — marine, non-predatory (sardines, anchovies, salmon, cod)
- Arsenic
- Aluminum
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Update history
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