|
|
|
|
LEADER |
01000naa a22002652 4500 |
001 |
NLM340742771 |
003 |
DE-627 |
005 |
20231226010147.0 |
007 |
cr uuu---uuuuu |
008 |
231226s2023 xx |||||o 00| ||eng c |
024 |
7 |
|
|a 10.1080/09593330.2022.2077134
|2 doi
|
028 |
5 |
2 |
|a pubmed24n1135.xml
|
035 |
|
|
|a (DE-627)NLM340742771
|
035 |
|
|
|a (NLM)35546108
|
040 |
|
|
|a DE-627
|b ger
|c DE-627
|e rakwb
|
041 |
|
|
|a eng
|
100 |
1 |
|
|a Straioto, Henrique
|e verfasserin
|4 aut
|
245 |
1 |
0 |
|a Modification of natural zeolite clinoptilolite and ITS application in the adsorption of herbicides
|
264 |
|
1 |
|c 2023
|
336 |
|
|
|a Text
|b txt
|2 rdacontent
|
337 |
|
|
|a ƒaComputermedien
|b c
|2 rdamedia
|
338 |
|
|
|a ƒa Online-Ressource
|b cr
|2 rdacarrier
|
500 |
|
|
|a Date Completed 23.10.2023
|
500 |
|
|
|a Date Revised 23.10.2023
|
500 |
|
|
|a published: Print-Electronic
|
500 |
|
|
|a Citation Status MEDLINE
|
520 |
|
|
|a The clinoptilolite natural zeolites (NZs) posses low herbicide adsorption capacity demanding acid-, alkali-, or salt chemical modifications that enhance its adsorption. However, this may affect the material structure and charge distribution. Alternatively, zeolites may be synthesized at a high cost and time-consuming process. Consequently, new methods, such as the hydrothermal method, for NZ modification needs to be studied. In this sense, a novel surface-modified zeolite (SMZ), using hexadecyltrimethylammonium bromide (CTAB), in acid media was produced by the hydrothermal method and applied for the adsorption of Atrazine (ATZ), Diuron (DIU) and 2,4-D. Commercial NZ and SMZ were characterized by SEM, XRD, TGA, FT-IR, AA spectroscopy, pHPZC, Zeta potential and N2-physisorption. The SMZ chosen for the adsorption experiments was the one with the highest modification yield and adsorption capacity obtained from a complete design of experiments (CTAB=0.74 ; D=12 Mesh; HCl=0.1 M; t=6 h and T=205 ºC). The adsorption experiments revealed that the SMZ adsorption capacity for the herbicide 2,4-D (qmax=9.02 mg/g) was greater than that obtained for ATZ (qmax=2.11 mg/g) and DIU (qmax=1.85 mg/g), which was explained by the presence of the hydroxyl group and by geometric characteristics of the 2,4-D. Adsorption models' fitting showed that the adsorption of 2,4-D onto SMZ were best described by pseudo-second order kinetic (k2=0.005-0.006 g/mg.min; qe,exp=7.122-8.614 mg/g) and Langmuir isothermal model (KL=0.283-0.499 L/mg; qm=7.167-7.995 mg/g). These results indicate that the hydrothermal method is a viable alternative to enable the use of NZs for the adsorption of emerging contaminants from wastewater
|
650 |
|
4 |
|a Journal Article
|
650 |
|
4 |
|a cationic surfactant
|
650 |
|
4 |
|a emerging contaminants
|
650 |
|
4 |
|a hydrothermal modification
|
650 |
|
4 |
|a pesticides
|
650 |
|
4 |
|a water treatment
|
650 |
|
7 |
|a Herbicides
|2 NLM
|
650 |
|
7 |
|a clinoptilolite
|2 NLM
|
650 |
|
7 |
|a 12173-10-3
|2 NLM
|
650 |
|
7 |
|a Zeolites
|2 NLM
|
650 |
|
7 |
|a 1318-02-1
|2 NLM
|
650 |
|
7 |
|a Cetrimonium
|2 NLM
|
650 |
|
7 |
|a Z7FF1XKL7A
|2 NLM
|
650 |
|
7 |
|a Surface-Active Agents
|2 NLM
|
650 |
|
7 |
|a Diuron
|2 NLM
|
650 |
|
7 |
|a 9I3SDS92WY
|2 NLM
|
650 |
|
7 |
|a 2,4-Dichlorophenoxyacetic Acid
|2 NLM
|
650 |
|
7 |
|a 2577AQ9262
|2 NLM
|
700 |
1 |
|
|a Viotti, Paula Valéria
|e verfasserin
|4 aut
|
700 |
1 |
|
|a Moura, Alexandre Amado de
|e verfasserin
|4 aut
|
700 |
1 |
|
|a Diório, Alexandre
|e verfasserin
|4 aut
|
700 |
1 |
|
|a Scaliante, Mara Heloisa Neves Olsen
|e verfasserin
|4 aut
|
700 |
1 |
|
|a Moreira, Wardleison Martins
|e verfasserin
|4 aut
|
700 |
1 |
|
|a Vieira, Marcelo Fernandes
|e verfasserin
|4 aut
|
700 |
1 |
|
|a Bergamasco, Rosângela
|e verfasserin
|4 aut
|
773 |
0 |
8 |
|i Enthalten in
|t Environmental technology
|d 1993
|g 44(2023), 26 vom: 12. Nov., Seite 3949-3964
|w (DE-627)NLM098202545
|x 1479-487X
|7 nnns
|
773 |
1 |
8 |
|g volume:44
|g year:2023
|g number:26
|g day:12
|g month:11
|g pages:3949-3964
|
856 |
4 |
0 |
|u http://dx.doi.org/10.1080/09593330.2022.2077134
|3 Volltext
|
912 |
|
|
|a GBV_USEFLAG_A
|
912 |
|
|
|a SYSFLAG_A
|
912 |
|
|
|a GBV_NLM
|
912 |
|
|
|a GBV_ILN_350
|
951 |
|
|
|a AR
|
952 |
|
|
|d 44
|j 2023
|e 26
|b 12
|c 11
|h 3949-3964
|