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Photodegradation of MO by different photocatalysts under visible-light irradiation (l ! 400 nm). A) UV/Vis spectra of MO solutions after adsorption. B) UV/Vis spectra of MO solutions after release of MO molecules by adding a 1.5 mol L À1 solution of NaNO 3 in ethanol/water A C H T U N G T R E N N U N G (1/1 v/v). C) UV/Vis spectra of MO solutions after irradiation for different times and then release of MO molecules. 

Photodegradation of MO by different photocatalysts under visible-light irradiation (l ! 400 nm). A) UV/Vis spectra of MO solutions after adsorption. B) UV/Vis spectra of MO solutions after release of MO molecules by adding a 1.5 mol L À1 solution of NaNO 3 in ethanol/water A C H T U N G T R E N N U N G (1/1 v/v). C) UV/Vis spectra of MO solutions after irradiation for different times and then release of MO molecules. 

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A facile anion-exchange precipitation method was used to synthesize bifunctional Ag/AgBr/Co-Ni-NO(3) layered double hydroxide (LDH) nanocomposites by adding AgNO(3) solution to a suspension of Co-Ni-Br LDH. The Ag/AgBr nanoparticles were highly dispersed on the sheets of Co-Ni-NO(3) LDH. The prepared nanocomposites were used to adsorb and photocata...

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Context 1
... by this method, it can be determined whether the adsorbed MO molecules in the LDH could be photodegraded during irra- diation. The bottom curve in Figure 6 shows the UV/Vis data of MO solution after adsorption by Ag/AgBr/Co-Ni- NO 3 , irradiation, and then addition of NaNO 3 solution. After adsorption for 20 min, almost all MO molecules were adsorbed. ...
Context 2
... shown in Figure 6, both Co-Ni-Br and Ag/AgBr show photocatalytic activity toward MO, but Ag/AgBr/Co-Ni- NO 3 displays the highest photocatalytic activity and de- grades almost all MO dye molecules in 120 min, while Ag/ AgBr and Co-Ni-Br repectively resulted in about 63 and 15 % degradation under visible-light irradiation for 120 min at an MO concentration of 25 mg L À1 . Thus, immobilizing Ag/AgBr nanoparticles on Co-Ni-NO 3 sheets greatly en- hanced the photocatalytic activity. ...
Context 3
... The above method can be used to prepare other LDH/Ag salt composites, such as AgCl/Co(OH) 2 , AgCl/Zn-Cr LDH, and Ag 2 WO 4 /Ni-Cr LDH. The XRD patterns (see Support- ing Information, Figures S4-S6) of the composites were www.chemeurj.org characterized, and preliminary results indicate that these composites were successfully prepared by this method, that is the method described herein is a general strategy to pre- pare LDH/silver salt composites. ...

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AbstractA facile anion‐exchange precipitation method was used to synthesize bifunctional Ag/AgBr/Co–Ni–NO3 layered double hydroxide (LDH) nanocomposites by adding AgNO3 solution to a suspension of Co–Ni–Br LDH. The Ag/AgBr nanoparticles were highly dispersed on the sheets of Co–Ni–NO3 LDH. The prepared nanocomposites were used to adsorb and photoca...

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... By osmotic swelling of the host material in the presence of a polar organic solvent for example formamide, the exfoliation of LDH can be accomplished, resulting in a colloidal suspension of negatively-charged LDH nanosheets. Various LDH nanosheets with significant compositional changes of M 2+ /M 3+ or M 4+ metal ions were described thus far, including binary Zn-Cr/Al/Ti/Fe-LDH [219][220][221][222][223][224][225], Co-Al/Fe/Ni-LDH [226][227][228], Table 1 Various g-C 3 N 4 hybrids for solar energy harvesting. ...
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... The incremental increase in global fuel conflict as a result of exhaustible energy resources, as well as unfavorable ecological situations owing to rapid urbanization and industrialization, has become a key obstacle in current era [1e10]. The semiconductors based artificial photosynthesis has been regarded as one of the most prestigious techniques in order to fix the global fuel crisis by gathering, transforming and storing sustainable energy for the generation of practicable energy in a wide range of ecological systems [11,12]. Although the visionary research in 1972, was firstly initiated by Fujishima and Honda regarding the splitting of water into oxygen (O 2 ) and hydrogen (H 2 ) as a byproduct onto the substrate of TiO 2 anode and Pt cathode based electrodes through UV light ( Fig. 1a) [13]. ...
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... And there usually have some difficulty to be separated for reuse them. In our previous work, we have prepared several kinds of photocatalytic nanomaterials, 1 3 such as Cu/g-C 3 N 4 based photocatalysts [21], layered double hydroxides based composites [22], Sn doped ZnO microspheres [23] and porous carbon-CeO 2 composites [24]. These photocatalysts showed enhanced photocatalytic activities. ...
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... Meanwhile, the photo-induced holes left in the valence band of CdO diffuse effectively to the surface of the catalyst and reacts with water to form OH * radicals. The O 2 * and OH * radicals are the reactive species that degrade the dye molecules with the release of CO 2 and H 2 O [35]. The chemical reactions involved in the photocatalytic mechanism of the CdO:Ag catalysts could be summarized as follows [36]: ...
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... The layers of layered In(OH) 3 stacked by hydrogen bonding; the interlayer distance is about 5 . However, the traditional single metal hydroxides M(OH) 2 , such as Mg(OH) 2 , b-Ni(OH) 2 , and b-Co(OH) 2 , [11] are always in the brucite structure; all M(OH) 6 octahedra share edges with their neighbors to produce 2D charge-neutral layers as shown in Figure 4 b ( Figure S5). Brucite-like Al(OH) 3 is slightly different, since only 2/3 metal sites are occupied compared with brucites, and its formula could also be written as Al 2/3 (OH) 2 ( Figure S6). ...
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All reported layered metal hydroxides have brucite‐like metal‐hydroxyl host layers and the discovery of other types of layered metal hydroxides can significantly extend the layered metal hydroxide families, which is meaningful in both theory and applications. Here through hydroperoxyl anion coordinated In3+ cations as a precursor, we synthesized layered indium hydroxide which only existed as a three‐dimensional cubic phase before. The layer of the product exhibits an unusual structure where In(OH)6 octahedra share edges and vertexes with each other to form layers, which is completely different from the common edges sharing brucite‐like metal‐hydroxyl layer. By investigating the formation mechanism, the new layered structure is found to be formed by changing the traditional crystallization path through the hydroperoxyl anion coordinated intermediates. Many other new phases could also be discovered by following the same intrinsic principle.
... With the substrates as dispersing templates, homogeneous and uniform semiconductor crystal morphology could be formed, which in turn can enhance their photocatalytic performance [327][328][329][330][331][332][333][334]. The graphene sheets with high optical transmittance, large 2D specific surface area, unique electronic properties and locally conjugated aromatic system has regarded as one kind of ideal substrate candidates for photocatalytic deposition. ...
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... Besides, in all spectra, the existence of other bands at wavenumbers below 1000 cm −1 can be explained by the transitional mode vibrations of metal-O and metal-O-metal [27]. As shown in Fig. 2A (a), for the LDH-NO 3 , an absorption band is observed at 1384 cm −1 , which is caused by the fact that nitrate anions are present in the structure [55]. As represented in Fig. 2A (b), concerning AR-27/LDH, almost no absorption band of NO 3 − anion can be seen. ...
... Such anion-exchangeable ability enables the LDHs to be widely applied in anion adsorption materials with large adsorption capacity [22]. For example, in our previous research [23], Br intercalated Co-Ni LDHs nanosheets showed adsorption capacity of 195 mg g À 1 for methyl orange, much higher than that of commercial activated carbon (20-80 mesh) with 140 mg g À 1 . The intercalated anions can be further exchanged out of the interlayer of LDHs, which can react with metal ions to form products with different colors [24,25]. ...
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In this work, a novel approach for facile and rapid detection of heavy metal ions using anion-intercalated layered double hydroxides (LDHs) modified test strips is demonstrated. By intercalating Fe(CN)64- or S2- anions into the interlayers of LDHs on the filter paper, various heavy metal ions can be easily detected based on the color change before and after reaction between the anions and the heavy metal ions. Upon the dropping of heavy metal ions solutions to the test strips, the colors of the test strips changed instantly, which can be easily observed by naked eyes. With the decrease of the concentration, the color depth changed obviously. The lowest detection concentration can be up to 1×10-6 mol L-1. Due to the easily intercalation of anions into the interlayer of the LDHs on test trips, this procedure provides a general method for the construction of LDHs modified test strips for detection of heavy metal ions. The stability of the prepared test strips is investigated. Furthermore, all the results were highly reproducible. The test strips may have potential applications in environmental monitoring fields.