|
|
|
|
LEADER |
01000caa a22002652 4500 |
001 |
NLM260748862 |
003 |
DE-627 |
005 |
20250220051552.0 |
007 |
cr uuu---uuuuu |
008 |
231224s2016 xx |||||o 00| ||eng c |
024 |
7 |
|
|a 10.2175/106143016X14504669768813
|2 doi
|
028 |
5 |
2 |
|a pubmed25n0869.xml
|
035 |
|
|
|a (DE-627)NLM260748862
|
035 |
|
|
|a (NLM)27225782
|
040 |
|
|
|a DE-627
|b ger
|c DE-627
|e rakwb
|
041 |
|
|
|a eng
|
100 |
1 |
|
|a Wenke, Axel
|e verfasserin
|4 aut
|
245 |
1 |
0 |
|a Potential of Brass to Remove Inorganic Hg(II) from Aqueous Solution through Amalgamation
|
264 |
|
1 |
|c 2016
|
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 09.08.2016
|
500 |
|
|
|a Date Revised 26.05.2016
|
500 |
|
|
|a published: Print
|
500 |
|
|
|a Citation Status MEDLINE
|
520 |
|
|
|a Brass shavings (CuZn45) were tested for their efficiency to remove Hg(II) from contaminated groundwater through amalgamation. The study was focused on long-term retention efficiency, the understanding of the amalgamation process and kinetics, and influences of filter surface alteration. Column tests were performed with brass filters (thickness 3 to 9 cm) flushed with 1000 μg/L Hg solution for 8 hours under different flow rates (300 to 600 mL/h). Brass filters consistently removed >98% of Hg from solution independent of filter thickness and flow rate. In a long-term experiment (filter thickness 2 cm), Hg retention decreased from 96 to 92% within 2000 hours. Batch and column experiments for studying kinetics of Hg removal indicate ~100% Hg removal from solution within only 2 hours. Solid-phase mercury thermo-desorption analysis revealed that Hg(0) diffusion into the brass surface controls kinetics of mercury retention. Brass surface alteration could be observed, but did not influence Hg retention
|
650 |
|
4 |
|a Journal Article
|
650 |
|
4 |
|a Research Support, Non-U.S. Gov't
|
650 |
|
7 |
|a Water Pollutants, Chemical
|2 NLM
|
650 |
|
7 |
|a brass
|2 NLM
|
650 |
|
7 |
|a 12597-71-6
|2 NLM
|
650 |
|
7 |
|a Copper
|2 NLM
|
650 |
|
7 |
|a 789U1901C5
|2 NLM
|
650 |
|
7 |
|a Mercury
|2 NLM
|
650 |
|
7 |
|a FXS1BY2PGL
|2 NLM
|
650 |
|
7 |
|a Zinc
|2 NLM
|
650 |
|
7 |
|a J41CSQ7QDS
|2 NLM
|
700 |
1 |
|
|a Bollen, Anne
|e verfasserin
|4 aut
|
700 |
1 |
|
|a Richard, Jan-Helge
|e verfasserin
|4 aut
|
700 |
1 |
|
|a Biester, Harald
|e verfasserin
|4 aut
|
773 |
0 |
8 |
|i Enthalten in
|t Water environment research : a research publication of the Water Environment Federation
|d 1998
|g 88(2016), 6 vom: 25. Juni, Seite 531-9
|w (DE-627)NLM098214292
|x 1061-4303
|7 nnns
|
773 |
1 |
8 |
|g volume:88
|g year:2016
|g number:6
|g day:25
|g month:06
|g pages:531-9
|
856 |
4 |
0 |
|u http://dx.doi.org/10.2175/106143016X14504669768813
|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 88
|j 2016
|e 6
|b 25
|c 06
|h 531-9
|