|
|
|
|
LEADER |
01000caa a22002652 4500 |
001 |
NLM272330345 |
003 |
DE-627 |
005 |
20250221173027.0 |
007 |
cr uuu---uuuuu |
008 |
231224s2018 xx |||||o 00| ||eng c |
024 |
7 |
|
|a 10.1080/09593330.2017.1336574
|2 doi
|
028 |
5 |
2 |
|a pubmed25n0907.xml
|
035 |
|
|
|a (DE-627)NLM272330345
|
035 |
|
|
|a (NLM)28552012
|
040 |
|
|
|a DE-627
|b ger
|c DE-627
|e rakwb
|
041 |
|
|
|a eng
|
100 |
1 |
|
|a Veneu, Diego Macedo
|e verfasserin
|4 aut
|
245 |
1 |
0 |
|a Cadmium removal by bioclastic granules (Lithothamnium calcareum)
|b batch and fixed-bed column systems sorption studies
|
264 |
|
1 |
|c 2018
|
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 13.08.2018
|
500 |
|
|
|a Date Revised 02.12.2018
|
500 |
|
|
|a published: Print-Electronic
|
500 |
|
|
|a Citation Status MEDLINE
|
520 |
|
|
|a The potential of Bioclastic Granules - BG (calcium-carbonate-based material) using the algae Lithothamnium calcareum as sorbent for the removal of Cd(II) from aqueous solutions by sorption was evaluated through batch and continuous systems tests using a fixed-bed column. Sorption process variables, in particular pH (2-7), particle size (<38-300 μm), initial BG concentration (0.1-1.0 g L-1), initial Cd(II) concentrations (5-400 mg L-1) and contact time (5-240 min), were evaluated. Adsorption isotherm profiles of Cd(II) per BG were similar to an L-type, or Langmuir type, with the adsorption forming a monolayer of approximately 0.61 μm, with a qmax of 188.74 mg g-1 and kL of 0.710 L mg-1. Thomas's model considers that sorption is not limited to a chemical reaction but is controlled by mass transfer at the interface. In the present study, the obtained value of kTh was 0.895 mL h-1 mg-1, reaching a sorption capacity qo of 124.4 mg g-1. For the Yoon-Nelson model, it was possible to obtain two important parameters to describe the behavior of the column, the rate constant (kYN), obtaining a value of 0.09 h-1 and an τ of 82.12 h corresponding to the time required for sorption to occur of 50% of the solute in the rupture curve. X-ray diffraction and scanning electron microscopy analyses coupled to the X-ray dispersive energy system (SEM/EDS) of the BG after the Cd(II) ion sorption tests evidenced the formation of crystals with the prevalence of a new mineral phase (otavite)
|
650 |
|
4 |
|a Journal Article
|
650 |
|
4 |
|a Sorption
|
650 |
|
4 |
|a cadmium
|
650 |
|
4 |
|a carbonate minerals
|
650 |
|
4 |
|a heavy metal
|
650 |
|
4 |
|a otavite
|
650 |
|
7 |
|a Water Pollutants, Chemical
|2 NLM
|
650 |
|
7 |
|a Cadmium
|2 NLM
|
650 |
|
7 |
|a 00BH33GNGH
|2 NLM
|
700 |
1 |
|
|a Schneider, Claudio Luiz
|e verfasserin
|4 aut
|
700 |
1 |
|
|a de Mello Monte, Marisa Bezerra
|e verfasserin
|4 aut
|
700 |
1 |
|
|a Cunha, Osvaldo Galvão Caldas
|e verfasserin
|4 aut
|
700 |
1 |
|
|a Yokoyama, Lídia
|e verfasserin
|4 aut
|
773 |
0 |
8 |
|i Enthalten in
|t Environmental technology
|d 1998
|g 39(2018), 13 vom: 16. Juli, Seite 1670-1681
|w (DE-627)NLM098202545
|x 1479-487X
|7 nnns
|
773 |
1 |
8 |
|g volume:39
|g year:2018
|g number:13
|g day:16
|g month:07
|g pages:1670-1681
|
856 |
4 |
0 |
|u http://dx.doi.org/10.1080/09593330.2017.1336574
|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 39
|j 2018
|e 13
|b 16
|c 07
|h 1670-1681
|