{"id":614,"date":"2018-03-27T14:04:20","date_gmt":"2018-03-27T12:04:20","guid":{"rendered":"https:\/\/fractioncollector.info\/?page_id=614"},"modified":"2024-11-12T10:01:20","modified_gmt":"2024-11-12T08:01:20","slug":"publications","status":"publish","type":"page","link":"https:\/\/www.fractioncollector.info\/de\/publications\/","title":{"rendered":"Publications about fraction collectors &#038; autosamplers as references for LAMBDA OMNICOLL"},"content":{"rendered":"<div id=\"pl-614\"  class=\"panel-layout\" ><div id=\"pg-614-0\"  class=\"panel-grid panel-has-style\"  style=\"margin-bottom: 50px\" ><div class=\"siteorigin-panels-stretch panel-row-style-full-width panel-row-style panel-row-style-for-614-0\" style=\"padding: 0px 0px 0px 0px;\" data-stretch-type=\"full-width-stretch\" ><div id=\"pgc-614-0-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-0-0-0\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce panel-first-child panel-last-child\" data-index=\"0\" ><div style=\"padding: 50px 50px 50px 50px;\" class=\"panel-widget-style panel-widget-style-for-614-0-0-0\" ><div class=\"textwidget\"><h1 style=\"color: white; text-align: center; font-size: 35px; text-shadow: 1px 1px #000000; line-height: 100%;\">PUBLICATIONS ABOUT FRACTION COLLECTORS &amp; AUTOSAMPLERS<\/h1>\n<p style=\"text-align: center; text-shadow: 1px 1px #000000; line-height: 100%;\">Scientific papers and publications mentioning LAMBDA OMNICOLL<\/p>\n<\/div><\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-1\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 50px\" ><div id=\"pgc-614-1-0\"  class=\"panel-grid-cell\" ><div style=\"padding: 40px 40px 40px 40px;\" class=\"panel-cell-style panel-cell-style-for-614-1-0\" ><div id=\"panel-614-1-0-0\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce panel-first-child\" data-index=\"1\" style=\"margin-bottom: 50px\" ><div class=\"textwidget\"><p>The latest<strong> scientific publications as references<\/strong> about the LAMBDA OMNICOLL fraction collectors &amp; autosamplers are linked <a href=\"#2024\">below<\/a>. Further references are listed on <a href=\"https:\/\/www.lambda-instruments.com\/fraction-collector\/#publications\" target=\"_blank\" rel=\"noopener\">www.lambda-instruments.com\/fraction-collector\/#publications.<\/a><\/p>\n<\/div><\/div><div id=\"panel-614-1-0-1\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce\" data-index=\"2\" style=\"margin: 20px 20px 20px 20px;\" ><div class=\"textwidget\"><p style=\"padding-left: 5px; text-align: center; font-size: 20px;\"><span style=\"color: #333333;\"><em>\u00ab The best references for<br \/>\nfraction collectors &amp; autosamplers<br \/>\nare successful applications. \u00bb<\/em><\/span><\/p>\n<\/div><\/div><div id=\"panel-614-1-0-2\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce panel-last-child\" data-index=\"3\" ><div class=\"textwidget\"><p>We at LAMBDA Laboratory Instruments are always happy to receive your publications where LAMBDA OMNICOLL supports you in your projects in <strong>analytical, chemical &amp; life science laboratories.<\/strong><\/p>\n<\/div><\/div><\/div><\/div><div id=\"pgc-614-1-1\"  class=\"panel-grid-cell\" ><div style=\"padding: 0px 40px 0px 40px;\" class=\"panel-cell-style panel-cell-style-for-614-1-1\" ><div id=\"panel-614-1-1-0\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce panel-first-child panel-last-child\" data-index=\"4\" ><div class=\"textwidget\"><p><img loading=\"lazy\" decoding=\"async\" class=\"wp-image-1267 size-medium alignright\" src=\"https:\/\/www.fractioncollector.info\/wp-content\/uploads\/cropped-LAMBDA-laboratory-instruments-278x278.png\" alt=\"\" width=\"278\" height=\"278\" srcset=\"https:\/\/www.fractioncollector.info\/wp-content\/uploads\/cropped-LAMBDA-laboratory-instruments-278x278.png 278w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/cropped-LAMBDA-laboratory-instruments-150x150.png 150w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/cropped-LAMBDA-laboratory-instruments-270x270.png 270w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/cropped-LAMBDA-laboratory-instruments-192x192.png 192w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/cropped-LAMBDA-laboratory-instruments-180x180.png 180w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/cropped-LAMBDA-laboratory-instruments-32x32.png 32w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/cropped-LAMBDA-laboratory-instruments.png 512w\" sizes=\"auto, (max-width: 278px) 100vw, 278px\" \/> <\/p>\n<\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-2\"  class=\"panel-grid panel-has-style\"  style=\"margin-bottom: 50px\" ><div id=\"2023\" class=\"panel-row-style panel-row-style-for-614-2\" ><div id=\"pgc-614-2-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-2-0-0\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce panel-first-child panel-last-child\" data-index=\"5\" ><div style=\"padding: 25px 25px 25px 25px;\" id=\"2024\" class=\"panel-widget-style panel-widget-style-for-614-2-0-0\" ><div class=\"textwidget\"><h2 style=\"text-align: center;\"><span class=\"VIiyi\" lang=\"en\"><span class=\"JLqJ4b ChMk0b\"><span class=\"Q4iAWc\">2024: Publications about fraction collectors &amp; autosamplers<\/span><\/span><\/span><\/h2>\n<\/div><\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-3\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 50px\" ><div id=\"pgc-614-3-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-3-0-0\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce panel-first-child\" data-index=\"6\" style=\"margin-bottom: 50px\" ><h3 class=\"widget-title\">Ion exchange column chromatography: LAMBDA OMNICOLL was used for collecting 40 ml fractions <\/h3><div class=\"textwidget\"><p>Riemersma, M.C. (2024). <strong>Separation of terbium from gadolinium by solvent extraction, Upscaling terbium production for use in radionuclide therapy.<\/strong> TU Delft, Applied Sciences, Master thesis.<br \/>\n<a href=\"https:\/\/resolver.tudelft.nl\/uuid:d2dcd756-a4d2-4d3a-8709-7c537f41796b\" target=\"_blank\" rel=\"noopener\">https:\/\/resolver.tudelft.nl\/uuid:d2dcd756-a4d2-4d3a-8709-7c537f41796b<\/a> (2024 Nov. 08)<\/p>\n<p><strong>Keywords:<\/strong> separation, solvent extraction, gadolinium, terbium, DEHPA, MACROPA<\/p>\n<hr \/>\n<p>&nbsp;<\/p>\n<\/div><\/div><div id=\"panel-614-3-0-1\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce\" data-index=\"7\" style=\"margin-bottom: 50px\" ><div class=\"textwidget\"><h3>Dynamic membrane adsorption (flow-through mode, filtration area 3.8 cm<sup>2<\/sup>): Dynamic breakthrough experiments to investigate the influence of flux, NaCl and pH were run in duplicates and the permeate was collected by an automated LAMBDA OMNICOLL fraction sampler.<\/h3>\n<p>Wullenweber, J., Bennert, J., Mantel, T., &amp; Ernst, M. (2024). <strong>Characterizing Macroporous Ion Exchange Membrane Adsorbers for Natural Organic Matter (NOM) Removal\u2014Adsorption and Regeneration Behavior<\/strong>. Membranes, 14(6), 124.<br \/>\n<a href=\"https:\/\/doi.org\/10.3390\/membranes14060124\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.3390\/membranes14060124<\/a><\/p>\n<p><strong>Keywords:<\/strong> Membrane adsorber, ion-exchange membrane, adsorption, natural organic matter, NOM removal, water treatment, adsorptive membranes<\/p>\n<hr \/>\n<p>&nbsp;<\/p>\n<\/div><\/div><div id=\"panel-614-3-0-2\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce panel-last-child\" data-index=\"8\" ><h3 class=\"widget-title\">LAMBDA OMNICOLL facilitates the recuperation of desorbed fractions in a fixed-bed adsorption\u2013desorption setup (industrial prototype with two packed chromatograhy columns (stainless-steel, 50 mm \u00d7 20 mm, bed volume 15.71 ml))<\/h3><div class=\"textwidget\"><p>Bzainia, A., Igrejas, G., Pereira, M. J. V., Costa, M. R. P., &amp; Dias, R. C. (2024). <strong>Purification of stilbenes from grape stems in a continuous process based on photo-molecularly imprinted adsorbents and hydroalcoholic solvents.<\/strong> Separation and Purification Technology, 127798.<br \/>\n<a href=\"https:\/\/doi.org\/10.1016\/j.seppur.2024.127798\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.1016\/j.seppur.2024.127798<\/a><\/p>\n<p><strong>Keywords:<\/strong> pH, oxidation, flavonoids, food processing, conservation, bioactive compounds<\/p>\n<\/div><\/div><\/div><\/div><div id=\"pg-614-4\"  class=\"panel-grid panel-has-style\"  style=\"margin-bottom: 50px\" ><div id=\"2023\" class=\"panel-row-style panel-row-style-for-614-4\" ><div id=\"pgc-614-4-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-4-0-0\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce panel-first-child panel-last-child\" data-index=\"9\" ><div style=\"padding: 25px 25px 25px 25px;\" class=\"panel-widget-style panel-widget-style-for-614-4-0-0\" ><div class=\"textwidget\"><h2 style=\"text-align: center;\"><span class=\"VIiyi\" lang=\"en\"><span class=\"JLqJ4b ChMk0b\"><span class=\"Q4iAWc\">2023: Publications about fraction collectors &amp; autosamplers<\/span><\/span><\/span><\/h2>\n<\/div><\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-5\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 50px\" ><div id=\"pgc-614-5-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-5-0-0\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce panel-first-child\" data-index=\"10\" style=\"margin-bottom: 50px\" ><h3 class=\"widget-title\">At each 10-minute time interval, the effluent from the column was collected into 5 mL vials using a LAMBDA OMNICOLL fraction collector.<\/h3><div class=\"textwidget\"><p>Choudhary, A., Khandelwal, N., Ganie, Z. A., &amp; Darbha, G. K. (2023). <strong>Influence of magnetite and its weathering originated maghemite and hematite minerals on sedimentation and transport of nanoplastics in the aqueous and subsurface environments.<\/strong> Science of The Total Environment, 169132.<br \/>\n<a href=\"https:\/\/doi.org\/10.1016\/j.scitotenv.2023.169132\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.1016\/j.scitotenv.2023.169132<\/a><\/p>\n<p><strong>Keywords<\/strong>: persistent nanoplastics, iron oxide minerals, environment, magnetite, pH, humic acid, ionic strength, particle size, hematite, sedimentation kinetic<\/p>\n<p>LAMBDA OMNICOLL used for column chromatography in Environmental Nanoscience Laboratory, Darbha's research group:<br \/>\n<a href=\"https:\/\/gkdarbha.wixsite.com\/gopaladarbha\/instrumentation\" target=\"_blank\" rel=\"noopener\">https:\/\/gkdarbha.wixsite.com\/gopaladarbha\/instrumentation<\/a> (2024 Jan. 03)<br \/>\n<a href=\"https:\/\/static.wixstatic.com\/media\/11a26b_72ea880a9edb434ca34e530fef35c200~mv2.jpg\" target=\"_blank\" rel=\"noopener\">https:\/\/static.wixstatic.com\/media\/11a26b_72ea880a9edb434ca34e530fef35c200~mv2.jpg<\/a> (2024 Jan. 03)<br \/>\n<a href=\"https:\/\/static.wixstatic.com\/media\/11a26b_60f73569d1e443da848c87333dc7d8ca~mv2.png\/v1\/fill\/w_532,h_552,al_c,lg_1,q_85,enc_auto\/fraction%20pump.png\" target=\"_blank\" rel=\"noopener\">https:\/\/static.wixstatic.com\/media\/11a26b_60f73569d1e443da848c87333dc7d8ca~mv2.png\/v1\/fill\/w_532,h_552,al_c,lg_1,q_85,enc_auto\/fraction%20pump.png<\/a> (2024 Jan. 03)<\/p>\n<hr \/>\n<\/div><\/div><div id=\"panel-614-5-0-1\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce\" data-index=\"11\" style=\"margin-bottom: 50px\" ><h3 class=\"widget-title\">The sorption installation consisted of a peristaltic pump Ismatec IPC8 (flow rate 7.5 ml\/h), a glass sorption column (diameter 15 mm; 5 ml ion-exchange resin ) and an automatic fraction collector LAMBDA OMNICOLL.<\/h3><div class=\"textwidget\"><p>Skripchenko, S. Y., Nalivaiko, K. A., Titova, S. M., Rychkov, V. N., &amp; Semenishchev, V. S. (2023). <strong>Recovery of uranium from conversion production sludge by leaching with nitric acid and subsequent ion-exchange concentration<\/strong>. Hydrometallurgy, 106255.<br \/>\n<a href=\"https:\/\/doi.org\/10.1016\/j.hydromet.2023.106255\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.1016\/j.hydromet.2023.106255<\/a><\/p>\n<p><strong>Keywords:<\/strong> Uranium, near-surface storage facility, radioactive wastes, acid leaching, sorption, ammonium uranyl phosphate hydrate<\/p>\n<hr \/>\n<p>&nbsp;<\/p>\n<\/div><\/div><div id=\"panel-614-5-0-2\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce\" data-index=\"12\" style=\"margin-bottom: 50px\" ><h3 class=\"widget-title\">Simultaneous fraction collection: At five-minute intervals, samples were collected simutaneously from four column outlets using a LAMBDA OMNICOLL automatic fraction collector.<\/h3><div class=\"textwidget\"><p>Abdelrady, A., Tang, Y., Bogaard, T. &amp; Foppen, J. W. (2023). <strong>The Use of Silica Encapsulated DNA Particles with a Supermagnetic Iron Core (Sidnamag) in Sand Filtration System: Effect of Water Chemistry<\/strong>. Available at SSRN 4555357.<br \/>\n<a href=\"https:\/\/dx.doi.org\/10.2139\/ssrn.4555357\" target=\"_blank\" rel=\"noopener\">https:\/\/dx.doi.org\/10.2139\/ssrn.4555357<\/a> (04. December 2023)<\/p>\n<p><strong>Keywords:<\/strong> sand filtration system, tracer, DNA-tagged silica particles, solution chemistry, transport<\/p>\n<hr \/>\n<p>&nbsp;<\/p>\n<\/div><\/div><div id=\"panel-614-5-0-3\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce\" data-index=\"13\" style=\"margin-bottom: 50px\" ><h3 class=\"widget-title\">Gel permeation chromatography (GPC) with Superose 6 Increase 10\/300 GL column (GE Healthcare) on an HPLC system (Agilent\/Varian Prostar 210): Fractions were collected at the injection time point at 0.5 ml per fraction using a LAMBDA OMNICOLL fraction collector onto flat-bottom 96-deep-well plates (Costar 3599, Corning).<\/h3><div class=\"textwidget\"><p>Wannitikul, P., Wattana-Amorn, P., Sathitnaitham, S., Sakulkoo, J., Suttangkakul, A., Wonnapinij, P., W. Bassel, G.W., Simister, R., Leonardo D., Gomez, L.D &amp; Vuttipongchaikij, S. (2023). <strong>Disruption of a DUF247 Containing Protein Alters Cell Wall Polysaccharides and Reduces Growth in Arabidopsis.<\/strong> Plants, 12(10), 1977.<br \/>\n<a href=\"https:\/\/doi.org\/10.3390\/plants12101977\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.3390\/plants12101977<\/a><\/p>\n<p><strong>Keywords:<\/strong> DUF247, mannan, pectin, plant cell wall, plant growth, xylan, xyloglucan<\/p>\n<hr \/>\n<p>&nbsp;<\/p>\n<\/div><\/div><div id=\"panel-614-5-0-4\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce\" data-index=\"14\" style=\"margin-bottom: 50px\" ><h3 class=\"widget-title\">LAMBDA OMNICOLL fraction collector equipped with a peristaltic pump: For each soil column (length 22 cm, internal diameter 2.5 cm), 120 fractions were collected with a volume of 3 ml per fraction.<\/h3><div class=\"textwidget\"><p>Pena Silva, S. M. (2023). <strong>Estudio de los procesos de adsorci\u00f3n\/desorci\u00f3n de 2-isopropil-6-metil-4-pirimidinol (IMPH) y 3, 5, 6-tricloro-2-piridinol (TCP) en montmorillonita pilarizada mediante la inclusi\u00f3n de especies de [Fe, Al], Zr y Ti y su potencial uso en la mitigaci\u00f3n de lixiviaci\u00f3n desde suelos agr\u00edcolas.<\/strong><br \/>\n<a href=\"https:\/\/repositorio.uchile.cl\/handle\/2250\/195796\" target=\"_blank\" rel=\"noopener\">\u2028https:\/\/repositorio.uchile.cl\/handle\/2250\/195796<\/a> (01. December 2023)<\/p>\n<p><strong>Keywords<\/strong>: Montmorillonite, Soils Absorption and adsorption, Leaching<\/p>\n<hr \/>\n<p>&nbsp;<\/p>\n<\/div><\/div><div id=\"panel-614-5-0-5\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce\" data-index=\"15\" style=\"margin-bottom: 50px\" ><h3 class=\"widget-title\">Acid-washed sand (2.65 g\/cm3) column (2.7 x 8 cm) upward flow (0.40 mL\/min) DNAcol experiments: The effluent was collected continuously with a sampling period of 5 min using a LAMBDA OMNICOLL fraction collector.  <\/h3><div class=\"textwidget\"><p><a href=\"https:\/\/doi.org\/10.1016\/j.colsurfa.2023.132476\" target=\"_blank\" rel=\"noopener\"><img loading=\"lazy\" decoding=\"async\" class=\"wp-image-3625 size-medium alignright\" title=\"Kianfar, B.,Hassanizadeh, S. M., Abdelrady, A., Bogaard, T. &amp;amp; Foppen, J.W. (2023) Natural organic matter and ionic strength (CaCl2) affect transport, retention and remobilization of silica encapsulated DNA colloids (DNAcol) in saturated sand columns. Colloids and Surfaces A: Physicochemical and Engineering Aspects, 2023, 132476, ISSN 0927-7757,&lt;br \/&gt; https:\/\/doi.org\/10.1016\/j.colsurfa.2023.132476.\" src=\"https:\/\/www.fractioncollector.info\/wp-content\/uploads\/doi.org_10.1016_j.colsurfa.2023.132476-418x151.jpg\" alt=\"Kianfar, B.,Hassanizadeh, S. M., Abdelrady, A., Bogaard, T. &amp; Foppen, J.W. (2023) Natural organic matter and ionic strength (CaCl2) affect transport, retention and remobilization of silica encapsulated DNA colloids (DNAcol) in saturated sand columns. Colloids and Surfaces A: Physicochemical and Engineering Aspects, 2023, 132476, ISSN 0927-7757, https:\/\/doi.org\/10.1016\/j.colsurfa.2023.132476.\" width=\"418\" height=\"151\" srcset=\"https:\/\/www.fractioncollector.info\/wp-content\/uploads\/doi.org_10.1016_j.colsurfa.2023.132476-418x151.jpg 418w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/doi.org_10.1016_j.colsurfa.2023.132476-2000x722.jpg 2000w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/doi.org_10.1016_j.colsurfa.2023.132476-150x54.jpg 150w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/doi.org_10.1016_j.colsurfa.2023.132476-768x277.jpg 768w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/doi.org_10.1016_j.colsurfa.2023.132476-1536x555.jpg 1536w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/doi.org_10.1016_j.colsurfa.2023.132476-2048x739.jpg 2048w\" sizes=\"auto, (max-width: 418px) 100vw, 418px\" \/><\/a>Kianfar, B., Hassanizadeh, S. M., Abdelrady, A., Bogaard, T., &amp; Foppen, J. W. (2023). <strong>Natural organic matter and ionic strength (CaCl2) affect transport, retention and remobilization of silica encapsulated DNA colloids (DNAcol) in saturated sand columns.<\/strong> Colloids and Surfaces A: Physicochemical and Engineering Aspects, 678, 132476.<br \/>\n<a href=\"https:\/\/doi.org\/10.1016\/j.colsurfa.2023.132476\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.1016\/j.colsurfa.2023.132476<\/a>.<\/p>\n<p><strong>Keywords:<\/strong> Silica-encapsulated-DNA colloid (DNAcol); natural organic matter (NOM); ionic strength (CaCl2); remobilization; colloidal tracer; colloid transport<\/p>\n<hr \/>\n<p>&nbsp;<\/p>\n<\/div><\/div><div id=\"panel-614-5-0-6\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce\" data-index=\"16\" style=\"margin-bottom: 50px\" ><div id=\"labs-automation\" class=\"panel-widget-style panel-widget-style-for-614-5-0-6\" ><h3 class=\"widget-title\">Electrochemical reactions in flow setups with switching valve and LAMBDA OMNICOLL fraction collector (which can be operated with different sized collection vessels) as peripheral equipment for collecting electrolyte.<\/h3><div class=\"textwidget\"><p><a href=\"https:\/\/www.lambda-instruments.com\/news\/detail\/lambda-omnicoll-fraction-collector-used-in-the-automation-work\/\" target=\"_blank\" rel=\"noopener\"><img loading=\"lazy\" decoding=\"async\" class=\"alignright wp-image-3588\" title=\"LAMBDA OMNICOLL fraction collector for automation work\" src=\"https:\/\/www.fractioncollector.info\/wp-content\/uploads\/lambda-omnicoll-fraction-collector-automation-work-1024x1024.jpg\" alt=\"LAMBDA OMNICOLL fraction collector for automation work\" width=\"400\" height=\"400\" srcset=\"https:\/\/www.fractioncollector.info\/wp-content\/uploads\/lambda-omnicoll-fraction-collector-automation-work-1024x1024.jpg 1024w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/lambda-omnicoll-fraction-collector-automation-work-278x278.jpg 278w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/lambda-omnicoll-fraction-collector-automation-work-150x150.jpg 150w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/lambda-omnicoll-fraction-collector-automation-work-768x768.jpg 768w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/lambda-omnicoll-fraction-collector-automation-work.jpg 1080w\" sizes=\"auto, (max-width: 400px) 100vw, 400px\" \/><\/a><\/p>\n<p>Hielscher, M. M., D\u00f6rr, M., Schneider, J. &amp; Waldvogel S. R. (2023). <strong>LABS: Laboratory Automation and Batch Scheduling \u2013 A Modular Open Source Python Program for the Control of Automated Electrochemical Synthesis with a Web Interface.<\/strong> Chem. Asian J. 2023, e202300380.<br \/>\n<a href=\"https:\/\/doi.org\/10.1002\/asia.202300380\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.1002\/asia.202300380<\/a><\/p>\n<p><strong>Keywords:<\/strong> electrochemistry, automation, anodic oxidation, cheminformatics, phenol coupling reaction<\/p>\n<p><a href=\"https:\/\/www.lambda-instruments.com\/news\/detail\/lambda-omnicoll-fraction-collector-used-in-the-automation-work\/\" target=\"_blank\" rel=\"noopener\">www.lambda-instruments.com\/news\/detail\/lambda-omnicoll-fraction-collector-used-in-the-automation-work\/<\/a><\/p>\n<\/div><\/div><\/div><div id=\"panel-614-5-0-7\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce panel-last-child\" data-index=\"17\" ><div class=\"textwidget\"><hr \/>\n<h3>Influence of SDS and TX-100 surfactants on the vertical transport of the fungicide metabolite OH-CTL: at the top of the columns (1.8 cm (id) x 20 cm (h) PMMA, packed 18 cm (h) water-saturated soil &amp; top layer of surfactant-modified soil), 4 ml of OH-CTL solution (40 \u00b5g\/ml hydroxy chlorothalonil in water) were applied at a constant flow rate of 1 ml\/min. Then continuously leaching with 1 ml\/min water (UPW) until at least 10 or 40 pore volumes were collected. Fractions were taken on a LAMBDA OMNICOLL automated fraction collector.<\/h3>\n<p>B\u00e1ez, M. E., Sarkar, B., Pe\u00f1a, A., Vidal, J., Espinoza, J., &amp; Fuentes, E. (2023). E<strong>ffect of surfactants on the sorption-desorption, degradation, and transport of chlorothalonil and hydroxy-chlorothalonil in agricultural soils.<\/strong> Environmental Pollution, 327, 121545.<br \/>\n<a href=\"https:\/\/doi.org\/10.1016\/j.envpol.2023.121545\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.1016\/j.envpol.2023.121545<\/a><\/p>\n<p><strong>Keywords:<\/strong> chlorothalonil, CTL, hydroxy chlorothalonil, OH-CTL,\u00a0 soil remediation, surfactant, sorption-desorption, microorganisms, Triton X-100, sodium dodecyl sulphate, SDS, hexadecyltrimethylammonium bromide, HDTMA, Aerosol 22, Tween 80, degradation, volcanic soil, non-volcanic soil, fungicides, critical micellar concentration, pH, Kd<\/p>\n<\/div><\/div><\/div><\/div><div id=\"pg-614-6\"  class=\"panel-grid panel-has-style\"  style=\"margin-bottom: 50px\" ><div id=\"2022\" class=\"panel-row-style panel-row-style-for-614-6\" ><div id=\"pgc-614-6-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-6-0-0\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce panel-first-child panel-last-child\" data-index=\"18\" ><div style=\"padding: 25px 25px 25px 25px;\" class=\"panel-widget-style panel-widget-style-for-614-6-0-0\" ><div class=\"textwidget\"><h2 style=\"text-align: center;\"><span class=\"VIiyi\" lang=\"en\"><span class=\"JLqJ4b ChMk0b\"><span class=\"Q4iAWc\">2022: Publications about fraction collectors &amp; autosamplers<\/span><\/span><\/span><\/h2>\n<\/div><\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-7\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 50px\" ><div id=\"pgc-614-7-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-7-0-0\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce panel-first-child\" data-index=\"19\" style=\"margin-bottom: 50px\" ><h3 class=\"widget-title\">A LAMBDA OMNICOLL  fraction collector was placed at the Omnifit (lenght = 20 cm, inner diameter = 2.5 cm, PTFE end pieces) glass column outlet to recover the effluent fractions prior to further analyses.<\/h3><div class=\"textwidget\"><p>Cazals, F., Colombano, S., Huguenot, D., Betelu, S., Galopin, N., Perrault, A., Simonnot, M.-O., Ignatiadis, I., Rossano, S. &amp; Crampon, M. (2022). <strong>Polycyclic aromatic hydrocarbons remobilization from contaminated porous media by (bio) surfactants washing.<\/strong> Journal of Contaminant Hydrology, 251, 104065.<br \/>\n<a href=\"https:\/\/doi.org\/10.1016\/j.jconhyd.2022.104065\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.1016\/j.jconhyd.2022.104065<\/a><\/p>\n<p><strong>Keywords:<\/strong> Biosurfactant, Polycyclic Aromatic Hydrocarbons, CMC, PAHs removal, solubility, particulate transport; soil washing<\/p>\n<hr \/>\n<p>&nbsp;<\/p>\n<\/div><\/div><div id=\"panel-614-7-0-1\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce\" data-index=\"20\" style=\"margin-bottom: 50px\" ><h3 class=\"widget-title\">Adsorption tests in sand columns (PMMA, 3.2 cm diameter x 7.0 cm lenght): The effluent was collected with a fraction collector LAMBDA OMNICOLL to determine the Zn and Fe concentrations. <\/h3><div class=\"textwidget\"><p>Krok, B., Mohammadian, S., Noll, H. M., Surau, C., Markwort, S., Fritzsche, A., Fritzsche, A., Nachev, M., Sures, B. &amp; Meckenstock, R. U. (2022). <strong>Remediation of zinc-contaminated groundwater by iron oxide in situ adsorption barriers\u2013From lab to the field.<\/strong> Science of The Total Environment, 807, 151066.<br \/>\n<a href=\"https:\/\/doi.org\/10.1016\/j.scitotenv.2021.151066\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.1016\/j.scitotenv.2021.151066<\/a><\/p>\n<p><strong>Keywords of scientific publication:<\/strong> Nanoremediation, Heavy metals, Iron oxide nanoparticles, In situ remediation, Permeable barriers<\/p>\n<hr \/>\n<p>&nbsp;<\/p>\n<\/div><\/div><div id=\"panel-614-7-0-2\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce\" data-index=\"21\" style=\"margin-bottom: 50px\" ><h3 class=\"widget-title\">Samples were collected simultaneously using an automatic fraction collector LAMBDA OMNICOLL from the top of two PVC columns (15 cm, ID 2.1 cm; Milder) packed with 355\u2013425 \u00b5m diameter grain size quartz sand (Sibelco).<\/h3><div class=\"textwidget\"><p>Chakraborty, S., Foppen, J. W., &amp; Schijven, J. F. (2022).<strong> Effect of concentration of silica encapsulated ds-DNA colloidal microparticles on their transport through saturated porous media.<\/strong> Colloids and Surfaces A: Physicochemical and Engineering Aspects, Volume 651, 2022, 129625.<br \/>\n<a href=\"https:\/\/doi.org\/10.1016\/j.colsurfa.2022.129625\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.1016\/j.colsurfa.2022.129625<\/a><\/p>\n<p><strong>Keywords:<\/strong> Silica encapsulated, silica core dsDNA particles, injection concentration, saturated porous media, attachment rate, single collector removal efficiency.<\/p>\n<hr \/>\n<p>&nbsp;<\/p>\n<\/div><\/div><div id=\"panel-614-7-0-3\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce\" data-index=\"22\" style=\"margin-bottom: 50px\" ><h3 class=\"widget-title\">The flow velocity was maintained using a peristaltic pump. Treated effluents were collected at set time intervals using a programmable fraction collector (LAMBDA OMNICOLL single-stream collector).<\/h3><div class=\"textwidget\"><p>Feizi, F., Sarmah, A. K., Rangsivek, R. &amp; Gobindlal, K. (2022). <strong>Adsorptive removal of propranolol under fixed-bed column using magnetic tyre char: Effects of wastewater effluent organic matter and ball milling<\/strong>. Environmental Pollution, Volume 305, 2022, 119283, ISSN 0269-7491.<br \/>\n<a href=\"https:\/\/doi.org\/10.1016\/j.envpol.2022.119283\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.1016\/j.envpol.2022.119283<\/a><\/p>\n<p><strong>Keywords in publication:<\/strong> Magnetic tyre char, Fixed-bed column, Breakthrough curve, Effluent organic matter, HYDRUS-1D, Ball milling<\/p>\n<hr \/>\n<p>&nbsp;<\/p>\n<\/div><\/div><div id=\"panel-614-7-0-4\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce\" data-index=\"23\" style=\"margin-bottom: 50px\" ><h3 class=\"widget-title\">Effluents were collected in 2 h increments (corresponding to 7.5 PV, ca.5.4 mL) using a fraction collector (LAMBDA OMNICOLL), sealed in PP\u00a0bottles and refrigerated until analysis.\u00a0<\/h3><div class=\"textwidget\"><p>Perdrial, N., V\u00e1zquez-Ortega, A., Reinoso-Maset, E., O'Day, P. A. &amp; Chorover, J. (2022). <strong>Effects of flow on uranium speciation in soils impacted by acidic waste fluids.<\/strong>\u00a0Journal of Environmental Radioactivity, Volumes 251\u2013252, 2022, 106955, ISSN 0265-931X.<br \/>\n<a href=\"https:\/\/doi.org\/10.1016\/j.jenvrad.2022.106955\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.1016\/j.jenvrad.2022.106955<\/a><\/p>\n<p><strong>Keywords:<\/strong> Radionuclides, Phosphate, EXAFS, Thermodynamic modeling, Boltwoodite, Hanford site<\/p>\n<hr \/>\n<p>&nbsp;<\/p>\n<\/div><\/div><div id=\"panel-614-7-0-5\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce\" data-index=\"24\" style=\"margin-bottom: 50px\" ><h3 class=\"widget-title\">Dynamic sorption experiments were conducted in a fixed-bed column with 5 mL of RUA21207 resin. The solution was passed through a column at a 10 mL h\u2212 1 flow rate. Samples of the solution were taken at regular intervals (1 h) using the fraction collector &#038; autosampler LAMBDA OMNICOLL.<\/h3><div class=\"textwidget\"><p>Smyshlyaev, D., Kirillov, E., Kirillov, S., Bunkov, G., Rychkov, V., Botalov, M., Taukin, A., Yuldashbaeva, A. &amp; Malyshev, A. (2022). <strong>Recovery and separation of Sc, Zr and Ti from acidic sulfate solutions for high purity scandium oxide production: Laboratory and pilot study.<\/strong> Hydrometallurgy, Volume 211, 2022, 105889, ISSN 0304-386X.<br \/>\n<a href=\"https:\/\/doi.org\/10.1016\/j.hydromet.2022.105889\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.1016\/j.hydromet.2022.105889<\/a><\/p>\n<p><strong>Keywords:<\/strong> Zirconium, Titanium, Scandium, Separation, Ion exchange, Sulfate solutions<\/p>\n<hr \/>\n<p>&nbsp;<\/p>\n<\/div><\/div><div id=\"panel-614-7-0-6\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce\" data-index=\"25\" style=\"margin-bottom: 50px\" ><h3 class=\"widget-title\">Sorption with various resins was studied under dynamic conditions by passing the solution through an ion-exchange column; samples were taken by LAMBDA OMNICOLL fraction collector.<\/h3><div class=\"textwidget\"><p>Oqilov, B. R., Botalov, M. S., Rychkov, V. N. and Kirillov , E. V. (2022). <strong>Study of sorption leaching of scandium from red mud with Succinic acid.<\/strong> AIP Conference Proceedings 2466, 050025 (2022).<br \/>\n<a href=\"https:\/\/doi.org\/10.1063\/5.0092655\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.1063\/5.0092655<\/a><\/p>\n<p><strong>Keywords:<\/strong> Sorption leaching, leaching agent, resins, ion-exchange column, fraction collector, extraction, Sc, scandium, red mud, Succinic acid, transition metals<\/p>\n<hr \/>\n<p>&nbsp;<\/p>\n<\/div><\/div><div id=\"panel-614-7-0-7\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce\" data-index=\"26\" style=\"margin-bottom: 50px\" ><h3 class=\"widget-title\">The effluent was automatically sampled in fractions of 10 mL using a LAMBDA OMNICOLL fraction Collector. The desorption of heavy metal ions was also studied in dynamic conditions by passing a 0.1 M HCl aqueous solution through the column at a flow rate of 1 mL\/min.<\/h3><div class=\"textwidget\"><p>Dinu, M.V., Humelnicu, I., Ghiorghita, C.A. &amp; Humelnicu, D.\u00a0(2022). <strong>Aminopolycarboxylic Acids-Functionalized Chitosan-Based Composite Cryogels as Valuable Heavy Metal Ions Sorbents:\u00a0Fixed-Bed Column Studies and Theoretical Analysis<\/strong>.\u00a0Gels 2022, 8, 221.<br \/>\n<a href=\"https:\/\/doi.org\/10.3390\/gels8040221\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.3390\/gels8040221<\/a><\/p>\n<p><strong>Keywords:<\/strong> aminopolycarboxylic acids; chelating agents; theoretical analysis; fixed-bed column studies; multicomponent heavy metal ions solution<\/p>\n<hr \/>\n<p>&nbsp;<\/p>\n<\/div><\/div><div id=\"panel-614-7-0-8\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce\" data-index=\"27\" style=\"margin-bottom: 50px\" ><h3 class=\"widget-title\">Soil column experiments were conducted with adjustable-height\u00a0chromatography columns, made of borosilicate glass. For each experiment ~ 0.8 ml column effluent was collected in a 20 ml centrifuge tube using a fraction collector LAMBDA OMNICOLL.<\/h3><div class=\"textwidget\"><p>Kianfar, B., Tian, J., Rozemeijer, J., van der Zaan, B., Bogaard, T. A., &amp; Foppen, J. W. (2022). <strong>Transport characteristics of DNA-tagged silica colloids as a colloidal tracer in saturated sand columns; role of solution chemistry, flow velocity, and sand grain size.<\/strong> Journal of Contaminant Hydrology, 246, 103954.<br \/>\n<a href=\"https:\/\/doi.org\/10.1016\/j.jconhyd.2022.103954\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.1016\/j.jconhyd.2022.103954<\/a><\/p>\n<p><strong>Keywords:<\/strong> DNA-tagged silica colloids, Tracer, Solution chemistry<\/p>\n<hr \/>\n<p>&nbsp;<\/p>\n<\/div><\/div><div id=\"panel-614-7-0-9\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce panel-last-child\" data-index=\"28\" ><h3 class=\"widget-title\">The uranium sorption from model solutions in static mode was carrying out by use of anion-exchangers. The volume of resin loaded in the column was 5 ml, the filtration rate of solution through resin layer was 5 bed volume for 1 h. The filtrate at the outlet of the column was sampled by use of automatic fraction collector LAMBDA OMNICOLL.<\/h3><div class=\"textwidget\"><p>Nalivaiko, K., Skripchenko, S., Titova, S., &amp; Rychkov, V. (2022). <strong>Characterization and processing of radioactive uranium containing waste sludge by sulfuric acid leaching.<\/strong> Journal of Environmental Chemical Engineering, 10(1), 106972.<br \/>\n<a href=\"https:\/\/doi.org\/10.1016\/j.jece.2021.106972\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.1016\/j.jece.2021.106972<\/a><\/p>\n<div id=\"key0005\" class=\"keyword\"><strong>Keywords:<\/strong> Tailing Dump, Recycling, Specific Activity, Sorption<\/div>\n<\/div><\/div><\/div><\/div><div id=\"pg-614-8\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 50px\" ><div id=\"pgc-614-8-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-8-0-0\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce panel-first-child panel-last-child\" data-index=\"29\" ><div style=\"padding: 25px 25px 25px 25px;\" class=\"panel-widget-style panel-widget-style-for-614-8-0-0\" ><div class=\"textwidget\"><h2 style=\"text-align: center;\"><span class=\"VIiyi\" lang=\"en\"><span class=\"JLqJ4b ChMk0b\"><span class=\"Q4iAWc\">2021: Publications about fraction collectors &amp; autosamplers<\/span><\/span><\/span><\/h2>\n<\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-9\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 50px\" ><div id=\"pgc-614-9-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-9-0-0\" class=\"so-panel widget widget_sow-editor panel-first-child panel-last-child\" data-index=\"30\" ><div style=\"padding: 0px 0px 0px 0px;\" class=\"panel-widget-style panel-widget-style-for-614-9-0-0\" ><div\n\t\t\t\n\t\t\tclass=\"so-widget-sow-editor so-widget-sow-editor-base\"\n\t\t\t\n\t\t>\n<div class=\"siteorigin-widget-tinymce textwidget\">\n\t<h3><strong>Programmed LAMBDA OMNICOLL single-stream collector for collecting 3 mL of aqueous solutions at the outlet of a column at set time intervals.\u00a0<\/strong><\/h3>\n<p>Feizi, F., Sarmah,A.K. &amp; Rangsivek, R. (2021).\u00a0<strong>Adsorption of pharmaceuticals in a fixed-bed column using tyre-based activated carbon: Experimental investigations and numerical modelling<\/strong>. Journal of Hazardous Materials, 2021.<\/p>\n<p><a title=\"https:\/\/doi.org\/10.1016\/j.jhazmat.2021.126010\" href=\"https:\/\/doi.org\/10.1016\/j.jhazmat.2021.126010\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.1016\/j.jhazmat.2021.126010<\/a><\/p>\n<hr \/>\n<h3><strong>Effluent solutions were collected with the fraction collector LAMBDA OMNICOLL.\u00a0<\/strong><\/h3>\n<p>V\u00e1zquez-Ortega, A., Perdrial, N., Reinoso-Maset, E., Root, R. A., O\u2019Day, P. A. &amp; Chorover, J. (2021).\u00a0<strong>Phosphate controls uranium release from acidic waste-weathered Hanford sediments<\/strong>. Journal of Hazardous Materials, Volume 416, 2021, 126240, ISSN 0304-3894.<\/p>\n<p><a title=\"https:\/\/doi.org\/10.1016\/j.jhazmat.2021.126240\" href=\"https:\/\/doi.org\/10.1016\/j.jhazmat.2021.126240\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.1016\/j.jhazmat.2021.126240<\/a><\/p>\n<hr \/>\n<h3><strong>The elute was collected using LAMBDA OMNICOLL fraction collector in 15 mL vials at a regular time interval and analyzed for concentrations in the effluents.<\/strong><\/h3>\n<p>Khandelwal, N., Tiwari, E., Singh, N., &amp; Darbha, G. K. (2021). <strong>Heterogeneously Porous Multiadsorbent Clay\u2013Biochar Surface to Support Redox-Sensitive Nanoparticles: Applications of Novel Clay\u2013Biochar\u2013Nanoscale Zerovalent Iron Nanotrident (C-BC-nZVI) in Continuous Water Filtration.<\/strong> ACS ES&amp;T Water, 1(3), 641-652.<br \/>\n<a href=\"https:\/\/doi.org\/10.1021\/acsestwater.0c00147\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.1021\/acsestwater.0c00147<\/a><\/p>\n<p><strong>Keywords:<\/strong>\u00a0remediation, nanocomposite, REE extraction, toxic metal sorption, dye removal, water purification, nanoadsorbent, column separation<\/p>\n<\/div>\n<\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-10\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 50px\" ><div id=\"pgc-614-10-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-10-0-0\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce panel-first-child panel-last-child\" data-index=\"31\" ><div style=\"padding: 25px 25px 25px 25px;\" class=\"panel-widget-style panel-widget-style-for-614-10-0-0\" ><div class=\"textwidget\"><h2 style=\"text-align: center;\"><span class=\"VIiyi\" lang=\"en\"><span class=\"JLqJ4b ChMk0b\"><span class=\"Q4iAWc\">2020: Publications about fraction collectors &amp; autosamplers<\/span><\/span><\/span><\/h2>\n<\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-11\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 50px\" ><div id=\"pgc-614-11-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-11-0-0\" class=\"so-panel widget widget_sow-editor panel-first-child panel-last-child\" data-index=\"32\" ><div style=\"padding: 0px 0px 0px 0px;\" class=\"panel-widget-style panel-widget-style-for-614-11-0-0\" ><div\n\t\t\t\n\t\t\tclass=\"so-widget-sow-editor so-widget-sow-editor-base\"\n\t\t\t\n\t\t>\n<div class=\"siteorigin-widget-tinymce textwidget\">\n\t<h3><strong>Dynamic Sorption Studies: A fraction collector LAMBDA OMNICOLL collected effluent samples every 15 min. Elution of heavy metal ions (HMIs) was performed by passing of 0.1 M HCl through the fixed-bed column with a flow velocity of 0.42 ml\/min.<\/strong><\/h3>\n<p>Humelnicu, D., Dragan, E. S., Ignat, M., &amp; Dinu, M. V. (2020). <strong>A comparative study on Cu2+, Zn2+, Ni2+, Fe3+, and Cr3+ metal ions removal from industrial wastewaters by chitosan-based composite cryogels.<\/strong> Molecules, 25(11), 2664.<br \/>\n<a href=\"https:\/\/doi.org\/10.3390\/molecules25112664\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.3390\/molecules25112664<\/a><\/p>\n<p><strong>Keywords:<\/strong> Chitosan, zeolite, cryogel sorbents, dynamic study, metal ions removak<\/p>\n<hr \/>\n<h3><strong>LAMBDA OMNICOLL Fraction Collector enabled the sampling of defined depth intervals. It is positioned in a glovebox using Argon to prevent re-oxidation of the samples<\/strong>.<\/h3>\n<p>Schroeder, H., Duester, L., Fabricius, A.-L., Ecker, D., Breitung, V. &amp; Ternes, T.A. (2020). <strong>Sediment water (interface) mobility of metal(loid)s and nutrients under undisturbed conditions and during resuspension. <\/strong>Journal of Hazardous Materials, 19\/03\/2020;<br \/>\n<a href=\"https:\/\/doi.org\/10.1016\/j.jhazmat.2020.122543\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.1016\/j.jhazmat.2020.122543<\/a><\/p>\n<p><strong>Keywords:<\/strong>\u00a0Pore water depth profiles, ICP-QQQ-MS, Peeper, Mobilization, Multi-element<\/p>\n<hr \/>\n<h3><strong>During the firn core melting process in a clean booth (ISO 5), the remaining sample stream from the debubbler was collected with a liquid fraction collector LAMBDA OMNICOLL (~0.7 mL\/min) as an archive of the meltwater.<\/strong><\/h3>\n<p>Seokhyun Ro, S., Hur, S. D., Hong, S., Chang, Ch., Moon, J., Han, Y., Jun, S. J., Hwang, H. &amp; Hong, S. (2020). <strong>An improved ion chromatography system coupled with a melter for highresolution ionic species reconstruction in Antarctic firn cores.<\/strong> Microchemical Journal, Elsevier, MICROC 105377;\u00a0<a href=\"https:\/\/doi.org\/10.1016\/j.microc.2020.105377\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.1016\/j.microc.2020.105377<\/a><\/p>\n<p><strong>Keywords:<\/strong>\u00a0on-line multi-ion chromatography system; firn core melter; fluoride ion; methanesulfonate ion; Styx Glacier; Antarctica.<\/p>\n<hr \/>\n<h3><strong>LAMBDA OMNICOLL connected to a HPLC column - by using a valve and a capillary - for collecting 2 ml fractions in 96 small scintillation vials (capacity of ~6 mL).<\/strong><\/h3>\n<p>Gaugler, P., Gaugler, V., Kamleitner, M. &amp; Schaaf, G. (2020).\u00a0<strong>Extraction and Quantification of Soluble, Radiolabeled Inositol Polyphosphates from Different Plant Species using SAX-HPLC.<\/strong>\u00a0Department of Plant Nutrition, Institute of Crop Science and Resource Conservation, University of Bonn;\u00a0<a href=\"https:\/\/doi.org\/10.3791\/61495\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.3791\/61495<\/a><\/p>\n<p><strong>Keywords:<\/strong>\u00a0SAX-HPLC column, valve, scintillation vials, 2 ml fractions<\/p>\n<\/div>\n<\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-12\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 50px\" ><div id=\"pgc-614-12-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-12-0-0\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce panel-first-child panel-last-child\" data-index=\"33\" ><div style=\"padding: 25px 25px 25px 25px;\" class=\"panel-widget-style panel-widget-style-for-614-12-0-0\" ><div class=\"textwidget\"><h2 style=\"text-align: center;\"><span class=\"VIiyi\" lang=\"en\"><span class=\"JLqJ4b ChMk0b\"><span class=\"Q4iAWc\">2019: Publications about fraction collectors &amp; autosamplers<\/span><\/span><\/span><\/h2>\n<\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-13\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 50px\" ><div id=\"pgc-614-13-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-13-0-0\" class=\"so-panel widget widget_sow-editor panel-first-child panel-last-child\" data-index=\"34\" ><div style=\"padding: 0px 0px 0px 0px;\" class=\"panel-widget-style panel-widget-style-for-614-13-0-0\" ><div\n\t\t\t\n\t\t\tclass=\"so-widget-sow-editor so-widget-sow-editor-base\"\n\t\t\t\n\t\t>\n<div class=\"siteorigin-widget-tinymce textwidget\">\n\t<h3><strong>To study the impact of mechanical disturbance and acidification on the metal(loid), LAMBDA OMNICOLL fraction collector is used to collect 12 profiles of 22 samples during each experiment.\u00a0<\/strong><\/h3>\n<p>Schroeder, H., Fabricius, A.-L., Ecker, D., Ternes, T.A. &amp; Duester, L. (2019).<strong> Impact of mechanical disturbance and acidification on the metal(loid) and C, P, S mobility at the sediment water interface examined using a fractionation meso profiling ICP-QQQ-MS approach.\u00a0<\/strong>Federal Institute of Hydrology, Division G \u2013 Qualitative Hydrology, Am Mainzer Tor 1, 56068 Koblenz, Germany.<br \/>\n<a href=\"https:\/\/doi.org\/10.1016\/j.scitotenv.2018.09.390\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.1016\/j.scitotenv.2018.09.390<\/a><\/p>\n<p><strong>Keywords:<\/strong>\u00a0Metal release, Pore water depth, profile Colloids Size, fractionation, Sediment water interface, Metalloid release.<\/p>\n<\/div>\n<\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-14\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 50px\" ><div id=\"pgc-614-14-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-14-0-0\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce panel-first-child panel-last-child\" data-index=\"35\" ><div style=\"padding: 25px 25px 25px 25px;\" class=\"panel-widget-style panel-widget-style-for-614-14-0-0\" ><div class=\"textwidget\"><h2 style=\"text-align: center;\"><span class=\"VIiyi\" lang=\"en\"><span class=\"JLqJ4b ChMk0b\"><span class=\"Q4iAWc\">2018: Publications about fraction collectors &amp; autosamplers<\/span><\/span><\/span><\/h2>\n<\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-15\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 50px\" ><div id=\"pgc-614-15-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-15-0-0\" class=\"so-panel widget widget_sow-editor panel-first-child panel-last-child\" data-index=\"36\" ><div style=\"padding: 0px 0px 0px 0px;\" class=\"panel-widget-style panel-widget-style-for-614-15-0-0\" ><div\n\t\t\t\n\t\t\tclass=\"so-widget-sow-editor so-widget-sow-editor-base\"\n\t\t\t\n\t\t>\n<div class=\"siteorigin-widget-tinymce textwidget\">\n\t<h3><strong>Perifusate fractions were collected using an LAMBDA OMNICOLL automated fraction collection system into 96-well MASTERBLOCK plates (Greiner bio-one) and at the end of the ex- periment stored at \u221280 \u00b0C<\/strong><\/h3>\n<p>Barlow, J., &amp; Solomon, T. P. (2019). <strong>Conditioned media from contracting skeletal muscle potentiates insulin secretion and enhances mitochondrial energy metabolism of pancreatic beta-cells.<\/strong> Metabolism, 91, 1-9.<br \/>\n<a href=\"https:\/\/doi.org\/10.1016\/j.metabol.2018.11.004\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.1016\/j.metabol.2018.11.004\u00a0<\/a><\/p>\n<p><strong>Keywords:\u00a0<\/strong>Pancreatic beta-cell insulin secretion, Type 2 diabetes, Mitochondrial function, Exercise, Skeletal muscle, Organ crosstalk<\/p>\n<p>&nbsp;<\/p>\n<\/div>\n<\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-16\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 50px\" ><div id=\"pgc-614-16-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-16-0-0\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce panel-first-child panel-last-child\" data-index=\"37\" ><div style=\"padding: 25px 25px 25px 25px;\" class=\"panel-widget-style panel-widget-style-for-614-16-0-0\" ><div class=\"textwidget\"><h2 style=\"text-align: center;\"><span class=\"VIiyi\" lang=\"en\"><span class=\"JLqJ4b ChMk0b\"><span class=\"Q4iAWc\">2017: Publications about fraction collectors &amp; autosamplers<\/span><\/span><\/span><\/h2>\n<\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-17\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 0px\" ><div id=\"pgc-614-17-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-17-0-0\" class=\"so-panel widget widget_sow-editor panel-first-child panel-last-child\" data-index=\"38\" ><div style=\"padding: 0px 0px 0px 0px;\" class=\"panel-widget-style panel-widget-style-for-614-17-0-0\" ><div\n\t\t\t\n\t\t\tclass=\"so-widget-sow-editor so-widget-sow-editor-base\"\n\t\t\t\n\t\t><h3 class=\"widget-title\">LAMBDA OMNICOLL fraction collector and LAMBDA PRECIFLOW peristaltic pump positioned in a glove box under an argon-atmosphere in a novel meso profiling and sampling system (messy) for biogeochemical studies of water pollution<\/h3>\n<div class=\"siteorigin-widget-tinymce textwidget\">\n\t<\/div>\n<\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-18\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 50px\" ><div id=\"pgc-614-18-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-18-0-0\" class=\"so-panel widget widget_sow-editor panel-first-child panel-last-child\" data-index=\"39\" ><div\n\t\t\t\n\t\t\tclass=\"so-widget-sow-editor so-widget-sow-editor-base\"\n\t\t\t\n\t\t>\n<div class=\"siteorigin-widget-tinymce textwidget\">\n\t<p>Schroeder, H., Fabricius, A. L., Ecker, D., Ternes, T. A., &amp; Duester, L. (2017). <strong>Metal (loid) speciation and size fractionation in sediment pore water depth profiles examined with a new meso profiling system.<\/strong> Chemosphere,\u00a0179, 185-193.<br \/>\nFederal Institute of Hydrology, Division G - Qualitative Hydrology, Koblenz, Germany.<br \/>\n<a href=\"https:\/\/doi.org\/10.1016\/j.chemosphere.2017.03.080\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.1016\/j.chemosphere.2017.03.080<\/a><\/p>\n<p><strong>Keywords:<\/strong> Sediment pore water, Depth profile, Sediment water interface, Profiling, Metals<\/p>\n<div id=\"attachment_1835\" style=\"width: 428px\" class=\"wp-caption alignnone\"><img aria-describedby=\"caption-attachment-1835\" loading=\"lazy\" decoding=\"async\" class=\"wp-image-1835 size-medium\" src=\"https:\/\/www.fractioncollector.info\/wp-content\/uploads\/Messy-set-up-OMNICOLL-fraction-collector-and-LAMBDA-PRECIFLOW-peristaltic-pump-positioned-in-a-glove-box-under-an-argon-atmosphere-418x220.jpg\" alt=\"Messy set-up-OMNICOLL fraction collector and LAMBDA PRECIFLOW peristaltic pump positioned in a glove box under an argon-atmosphere\" width=\"418\" height=\"220\" srcset=\"https:\/\/www.fractioncollector.info\/wp-content\/uploads\/Messy-set-up-OMNICOLL-fraction-collector-and-LAMBDA-PRECIFLOW-peristaltic-pump-positioned-in-a-glove-box-under-an-argon-atmosphere-418x220.jpg 418w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/Messy-set-up-OMNICOLL-fraction-collector-and-LAMBDA-PRECIFLOW-peristaltic-pump-positioned-in-a-glove-box-under-an-argon-atmosphere-150x79.jpg 150w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/Messy-set-up-OMNICOLL-fraction-collector-and-LAMBDA-PRECIFLOW-peristaltic-pump-positioned-in-a-glove-box-under-an-argon-atmosphere-768x405.jpg 768w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/Messy-set-up-OMNICOLL-fraction-collector-and-LAMBDA-PRECIFLOW-peristaltic-pump-positioned-in-a-glove-box-under-an-argon-atmosphere-720x380.jpg 720w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/Messy-set-up-OMNICOLL-fraction-collector-and-LAMBDA-PRECIFLOW-peristaltic-pump-positioned-in-a-glove-box-under-an-argon-atmosphere.jpg 1186w\" sizes=\"auto, (max-width: 418px) 100vw, 418px\" \/><p id=\"caption-attachment-1835\" class=\"wp-caption-text\">https:\/\/doi.org\/10.1016\/j.chemosphere.2017.03.080<\/p><\/div>\n<\/div>\n<\/div><\/div><\/div><div id=\"pgc-614-18-1\"  class=\"panel-grid-cell\" ><div id=\"panel-614-18-1-0\" class=\"so-panel widget widget_sow-editor panel-first-child panel-last-child\" data-index=\"40\" ><div style=\"padding: 0px 0px 30px 10px;\" class=\"panel-widget-style panel-widget-style-for-614-18-1-0\" ><div\n\t\t\t\n\t\t\tclass=\"so-widget-sow-editor so-widget-sow-editor-base\"\n\t\t\t\n\t\t>\n<div class=\"siteorigin-widget-tinymce textwidget\">\n\t<p style=\"font-size: 13px;\"><strong>Abstract:<\/strong> <em><strong>\"<\/strong>In an exemplary incubation study with an anaerobic sediment sampled at an oxbow of the river Lahn in Germany (50\u00b018\u203256.87\u2033N; 7\u00b037\u203241.25\u2033E) and contaminated by former mining activity, a novel meso profiling and sampling system messy is presented. Messy enables a low invasive, automated sampling of pore water profiles across the sediment water interface (SWI), down to \u223c20 cm depth with a spacial resolution of 1 cm. In parallel to the pore water sampling it measures physicochemical sediment parameters such as redox potential and pH value. In an incubation experiment of 151 days the ability of the setup was proven to address several different aspects relevant for fresh water and marine sediment studies: (i) The influence of mechanical disturbance and oxygen induced acidification on the mobility of 13 metals and metalloids (Cd, Co, Cu, Fe, Mn, Mo, Ni, Sb, U, V, Zn) was quantified based on 11 profiles. The analytes were quantified by inductively coupled plasma-mass spectrometry. Three groups of elements were identified with respect to the release into the pore water and the overlying water under different experimental conditions. (ii) The capability to investigate the impacts of changing physicochemical sediment properties on arsenic and antimony (III\/V) speciation is shown. (iii) An approach to obtain information on size fractionation effects and to address the colloidal pore water fractions (0.45 \u03bcm\u201316 \u03bcm) was successfully conducted for the elements Ag, As, Cu, Fe and Mn.\" <\/em>\u00a0(https:\/\/doi.org\/10.1016\/j.chemosphere.2017.03.080)<\/p>\n<\/div>\n<\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-19\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 50px\" ><div id=\"pgc-614-19-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-19-0-0\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce panel-first-child panel-last-child\" data-index=\"41\" ><div style=\"padding: 25px 25px 25px 25px;\" class=\"panel-widget-style panel-widget-style-for-614-19-0-0\" ><div class=\"textwidget\"><h2 style=\"text-align: center;\"><span class=\"VIiyi\" lang=\"en\"><span class=\"JLqJ4b ChMk0b\"><span class=\"Q4iAWc\">2016: Publications about fraction collectors &amp; autosamplers<\/span><\/span><\/span><\/h2>\n<\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-20\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 0px\" ><div id=\"pgc-614-20-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-20-0-0\" class=\"so-panel widget widget_sow-editor panel-first-child panel-last-child\" data-index=\"42\" ><div style=\"padding: 0px 0px 0px 0px;\" class=\"panel-widget-style panel-widget-style-for-614-20-0-0\" ><div\n\t\t\t\n\t\t\tclass=\"so-widget-sow-editor so-widget-sow-editor-base\"\n\t\t\t\n\t\t><h3 class=\"widget-title\">Automated sample collector LAMBDA OMNICOLL was used to collect effluent samples (10 ml\/min) from the packed bed column to evaluate the transport potential of stabilized milled ZVI particle suspensions<\/h3>\n<div class=\"siteorigin-widget-tinymce textwidget\">\n\t<\/div>\n<\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-21\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 50px\" ><div id=\"pgc-614-21-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-21-0-0\" class=\"so-panel widget widget_sow-editor panel-first-child panel-last-child\" data-index=\"43\" ><div\n\t\t\t\n\t\t\tclass=\"so-widget-sow-editor so-widget-sow-editor-base\"\n\t\t\t\n\t\t>\n<div class=\"siteorigin-widget-tinymce textwidget\">\n\t<p>Velimirovic, M., Schmid, D., Wagner, S., Mici\u0107, V., von der Kammer, F. &amp; Thilo Hofmann, T. (2016). <strong>Agar agar-stabilized milled zerovalent iron particles for in situ groundwater remediation. <\/strong>Science of The Total Environment.<br \/>\n<a href=\"https:\/\/doi.org\/10.1016\/j.scitotenv.2015.11.007\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.1016\/j.scitotenv.2015.11.007<\/a><\/p>\n<p><strong>Keywords:<\/strong>\u00a0Milled zerovalent iron, Agar agar, Particle stability, Particle transport, Particle reactivity<\/p>\n<p>&nbsp;<\/p>\n<div id=\"attachment_1842\" style=\"width: 428px\" class=\"wp-caption alignnone\"><img aria-describedby=\"caption-attachment-1842\" loading=\"lazy\" decoding=\"async\" class=\"wp-image-1842 size-medium\" src=\"https:\/\/www.fractioncollector.info\/wp-content\/uploads\/Agar-agar-stabilized-milled-zerovalent-iron-particles-for-in-situ-groundwater-remediation-418x146.jpg\" alt=\"Automated sample collector OMNICOLL was used to collect effluent samples (10 ml\/min) from the packed bed column to evaluate the transport potential of stabilized milled ZVI particle suspensions\" width=\"418\" height=\"146\" srcset=\"https:\/\/www.fractioncollector.info\/wp-content\/uploads\/Agar-agar-stabilized-milled-zerovalent-iron-particles-for-in-situ-groundwater-remediation-418x146.jpg 418w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/Agar-agar-stabilized-milled-zerovalent-iron-particles-for-in-situ-groundwater-remediation-150x53.jpg 150w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/Agar-agar-stabilized-milled-zerovalent-iron-particles-for-in-situ-groundwater-remediation-768x269.jpg 768w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/Agar-agar-stabilized-milled-zerovalent-iron-particles-for-in-situ-groundwater-remediation-2000x700.jpg 2000w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/Agar-agar-stabilized-milled-zerovalent-iron-particles-for-in-situ-groundwater-remediation-1080x380.jpg 1080w\" sizes=\"auto, (max-width: 418px) 100vw, 418px\" \/><p id=\"caption-attachment-1842\" class=\"wp-caption-text\">https:\/\/doi.org\/10.1016\/j.scitotenv.2015.11.007<\/p><\/div>\n<\/div>\n<\/div><\/div><\/div><div id=\"pgc-614-21-1\"  class=\"panel-grid-cell\" ><div id=\"panel-614-21-1-0\" class=\"so-panel widget widget_sow-editor panel-first-child panel-last-child\" data-index=\"44\" ><div style=\"padding: 0px 0px 30px 10px;\" class=\"panel-widget-style panel-widget-style-for-614-21-1-0\" ><div\n\t\t\t\n\t\t\tclass=\"so-widget-sow-editor so-widget-sow-editor-base\"\n\t\t\t\n\t\t>\n<div class=\"siteorigin-widget-tinymce textwidget\">\n\t<p style=\"font-size: 12px;\"><strong>Abstract:<\/strong> <em>\"Submicron-scale milled zerovalent iron (milled ZVI) particles produced by grinding macroscopic raw materials could provide a cost-effective alternative to nanoscale zerovalent iron (nZVI) particles for in situ degradation of chlorinated aliphatic hydrocarbons in groundwater. However, the aggregation and settling of bare milled ZVI particles from suspension presents a significant obstacle to their in situ application for groundwater remediation. In our investigations we reduced the rapid aggregation and settling rate of bare milled ZVI particles from suspension by stabilization with a \u201cgreen\u201d agar agar polymer. The transport potential of stabilized milled ZVI particle suspensions in a diverse array of natural heterogeneous porous media was evaluated in a series of well-controlled laboratory column experiments. The impact of agar agar on trichloroethene (TCE) removal by milled ZVI particles was assessed in laboratory-scale batch reactors. The use of agar agar significantly enhanced the transport of milled ZVI particles in all of the investigated porous media. Reactivity tests showed that the agar agar-stabilized milled ZVI particles were reactive towards TCE, but that their reactivity was an order of magnitude less than that of bare, non-stabilized milled ZVI particles. Our results suggest that milled ZVI particles could be used as an alternative to nZVI particles as their potential for emplacement into contaminated zone, their reactivity, and expected longevity are beneficial for in situ groundwater remediation.\" <\/em>(https:\/\/doi.org\/10.1016\/j.scitotenv.2015.11.007)<em><br \/>\n<\/em><\/p>\n<\/div>\n<\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-22\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 50px\" ><div id=\"pgc-614-22-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-22-0-0\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce panel-first-child panel-last-child\" data-index=\"45\" ><div style=\"padding: 25px 25px 25px 25px;\" class=\"panel-widget-style panel-widget-style-for-614-22-0-0\" ><div class=\"textwidget\"><h2 style=\"text-align: center;\"><span class=\"VIiyi\" lang=\"en\"><span class=\"JLqJ4b ChMk0b\"><span class=\"Q4iAWc\">2015: Publications about fraction collectors &amp; autosamplers<\/span><\/span><\/span><\/h2>\n<\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-23\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 0px\" ><div id=\"pgc-614-23-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-23-0-0\" class=\"so-panel widget widget_sow-editor panel-first-child panel-last-child\" data-index=\"46\" ><div style=\"padding: 0px 0px 0px 0px;\" class=\"panel-widget-style panel-widget-style-for-614-23-0-0\" ><div\n\t\t\t\n\t\t\tclass=\"so-widget-sow-editor so-widget-sow-editor-base\"\n\t\t\t\n\t\t><h3 class=\"widget-title\">Effluent samples were collected from the fixed bed column by the multi-stream LAMBDA OMNICOLL fraction collector to study the adsorption of selenite and selenate by Mg-Al-CO3 LDH in the continuous flow system<\/h3>\n<div class=\"siteorigin-widget-tinymce textwidget\">\n\t<\/div>\n<\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-24\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 50px\" ><div id=\"pgc-614-24-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-24-0-0\" class=\"so-panel widget widget_sow-editor panel-first-child panel-last-child\" data-index=\"47\" ><div\n\t\t\t\n\t\t\tclass=\"so-widget-sow-editor so-widget-sow-editor-base\"\n\t\t\t\n\t\t>\n<div class=\"siteorigin-widget-tinymce textwidget\">\n\t<p>Chubar, N. &amp; Szlachta, M. (2015). <strong>Static and dynamic adsorptive removal of selenite and selenate by alkoxide-free sol\u2013gel-generated Mg\u2013Al\u2013CO<sub>3<\/sub> layered double hydroxide: Effect of competing ions.<\/strong> Chemical Engineering Journal 279 (2015): 885-896.<br \/>\nUtrecht University, The Netherlands; Glasgow Caledonian University, UK &amp; Wroc\u0142aw University of Technology, Poland.<br \/>\n<a href=\"https:\/\/doi.org\/10.1016\/j.cej.2015.05.070\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.1016\/j.cej.2015.05.070<\/a><strong>\u00a0 <\/strong><\/p>\n<p><strong>Keywords:<\/strong>\u00a0Selenite, Selenate, Mg-Al layered double hydroxide, Batch adsorption, Dynamic adsorption, FTIR<\/p>\n<p>&nbsp;<\/p>\n<div id=\"attachment_1845\" style=\"width: 364px\" class=\"wp-caption alignleft\"><img aria-describedby=\"caption-attachment-1845\" loading=\"lazy\" decoding=\"async\" class=\"wp-image-1845 size-full\" src=\"https:\/\/www.fractioncollector.info\/wp-content\/uploads\/Multi-channel-LAMBDA-OMNICOLL-fraction-collector-to-study-the-adsorption-of-selenite-and-selenate.jpg\" alt=\"\" width=\"354\" height=\"200\" srcset=\"https:\/\/www.fractioncollector.info\/wp-content\/uploads\/Multi-channel-LAMBDA-OMNICOLL-fraction-collector-to-study-the-adsorption-of-selenite-and-selenate.jpg 354w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/Multi-channel-LAMBDA-OMNICOLL-fraction-collector-to-study-the-adsorption-of-selenite-and-selenate-150x85.jpg 150w\" sizes=\"auto, (max-width: 354px) 100vw, 354px\" \/><p id=\"caption-attachment-1845\" class=\"wp-caption-text\">https:\/\/doi.org\/10.1016\/j.cej.2015.05.070<\/p><\/div>\n<\/div>\n<\/div><\/div><\/div><div id=\"pgc-614-24-1\"  class=\"panel-grid-cell\" ><div id=\"panel-614-24-1-0\" class=\"so-panel widget widget_sow-editor panel-first-child panel-last-child\" data-index=\"48\" ><div style=\"padding: 0px 0px 30px 10px;\" class=\"panel-widget-style panel-widget-style-for-614-24-1-0\" ><div\n\t\t\t\n\t\t\tclass=\"so-widget-sow-editor so-widget-sow-editor-base\"\n\t\t\t\n\t\t>\n<div class=\"siteorigin-widget-tinymce textwidget\">\n\t<p style=\"font-size: 12px;\"><strong>Abstract:<\/strong> \"<em>Adsorption\/ion exchange is a major separation approach capable of recovering the valuable Se component from various multicomponent solutions or to reduce its concentration. In this study, we report a method for selenite and selenate adsorptive removal based on the application of Mg\u2013Al\u2013CO<sub>3<\/sub>\u00a0layered double hydroxide (LDH) generated via an alkoxide-free sol\u2013gel synthesis method developed by the authors. The selenite and selenate removal capability of Mg\u2013Al LDH was examined under static and dynamic adsorption conditions, focusing on the influence of the competing anions (phosphate, sulphate, carbonate, silicate, chloride). The adsorption capacities of Mg\u2013Al LDH for selenite and selenate obtained from the equilibrium isotherms were not influenced by the presence of the competing sulphate, retaining the highest values of 168 and 103\u00a0mg [Se]\/g<sub>dw<\/sub> for Se(IV) and Se(VI) at pH 5, respectively. This inorganic ion exchanger is capable of functioning across the broad range of pH values from 5 to 9. Mg\u2013Al LDH could purify 16,200 and 4200 bed volumes (BVs) of the selenite\/selenate-containing solutions (\u223c50 \u03bcg [Se]\/L initial concentration), respectively, until reaching a selenium concentration of zero in the effluents. The presence of phosphate and a 74-times higher concentration of sulphate compared with selenate or selenite in the adsorbate showed nearly no influence on the dynamic adsorptive performance of Mg\u2013Al LDH for selenite. An equivalent concentration of phosphate did not influence the dynamic adsorptive removal of selenate. Markedly higher concentrations of sulphate, however, decreased the time to breakthrough for selenate but did not affect the quality of its removal. Mg\u2013Al LDH is a promising inorganic ion exchanger for the removal of both of the aqueous selenium species and will be tested on industrial scales.\" <\/em>(https:\/\/doi.org\/10.1016\/j.cej.2015.05.070)<\/p>\n<\/div>\n<\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-25\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 50px\" ><div id=\"pgc-614-25-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-25-0-0\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce panel-first-child panel-last-child\" data-index=\"49\" ><div style=\"padding: 25px 25px 25px 25px;\" class=\"panel-widget-style panel-widget-style-for-614-25-0-0\" ><div class=\"textwidget\"><h2 style=\"text-align: center;\"><span class=\"VIiyi\" lang=\"en\"><span class=\"JLqJ4b ChMk0b\"><span class=\"Q4iAWc\">2014: Publications about fraction collectors &amp; autosamplers<\/span><\/span><\/span><\/h2>\n<\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-26\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 0px\" ><div id=\"pgc-614-26-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-26-0-0\" class=\"so-panel widget widget_sow-editor panel-first-child panel-last-child\" data-index=\"50\" ><div style=\"padding: 0px 0px 0px 0px;\" class=\"panel-widget-style panel-widget-style-for-614-26-0-0\" ><div\n\t\t\t\n\t\t\tclass=\"so-widget-sow-editor so-widget-sow-editor-base\"\n\t\t\t\n\t\t><h3 class=\"widget-title\">Effluent from the glass chromatography column was collected by the LAMBDA OMNICOLL fraction collector to study ion-exchange reactions between Na+, H+, and Ca2+ under dynamic conditions<\/h3>\n<div class=\"siteorigin-widget-tinymce textwidget\">\n\t<\/div>\n<\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-27\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 50px\" ><div id=\"pgc-614-27-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-27-0-0\" class=\"so-panel widget widget_sow-editor panel-first-child panel-last-child\" data-index=\"51\" ><div\n\t\t\t\n\t\t\tclass=\"so-widget-sow-editor so-widget-sow-editor-base\"\n\t\t\t\n\t\t>\n<div class=\"siteorigin-widget-tinymce textwidget\">\n\t<p>Lu, J., Tertre, E., &amp; Beaucaire, C. (2014).\u00a0<strong>Assessment of a predictive model to describe the migration of major inorganic cations in a Bt soil horizon. <\/strong>Applied Geochemistry, Volume 41, February 2014, Pages 151-162.<br \/>\nCEA, DANS\/DPC\/SECR\/L3MR and Universit\u00e9 de Poitiers-CNRS, France.<br \/>\n<a href=\"https:\/\/doi.org\/10.1016\/j.apgeochem.2013.12.009\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.1016\/j.apgeochem.2013.12.009<\/a><\/p>\n<p><strong>Keywords:<\/strong> Ion-exchange reactions; Cationic Exchange Capacity (CEC); Ion chromatography; Bt horizon; Packed column; Wyoming montmorillonite; Reactive transport model, Metallic cation, Sediment, Ion exchange model, Reversible sorption<\/p>\n<p>&nbsp;<\/p>\n<div id=\"attachment_1850\" style=\"width: 278px\" class=\"wp-caption alignnone\"><img aria-describedby=\"caption-attachment-1850\" loading=\"lazy\" decoding=\"async\" class=\"wp-image-1850 size-full\" src=\"https:\/\/www.fractioncollector.info\/wp-content\/uploads\/The-effluent-was-collected-by-OMNICOLL-fraction-collector-to-describe-reactive-transport-of-major-cations-in-a-soil-horizon.jpg\" alt=\"The effluent was collected by OMNICOLL fraction collector to describe reactive transport of major cations in a soil horizon\" width=\"268\" height=\"200\" srcset=\"https:\/\/www.fractioncollector.info\/wp-content\/uploads\/The-effluent-was-collected-by-OMNICOLL-fraction-collector-to-describe-reactive-transport-of-major-cations-in-a-soil-horizon.jpg 268w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/The-effluent-was-collected-by-OMNICOLL-fraction-collector-to-describe-reactive-transport-of-major-cations-in-a-soil-horizon-150x112.jpg 150w\" sizes=\"auto, (max-width: 268px) 100vw, 268px\" \/><p id=\"caption-attachment-1850\" class=\"wp-caption-text\">https:\/\/doi.org\/10.1016\/j.apgeochem.2013.12.009<\/p><\/div>\n<\/div>\n<\/div><\/div><\/div><div id=\"pgc-614-27-1\"  class=\"panel-grid-cell\" ><div id=\"panel-614-27-1-0\" class=\"so-panel widget widget_sow-editor panel-first-child panel-last-child\" data-index=\"52\" ><div style=\"padding: 0px 0px 30px 10px;\" class=\"panel-widget-style panel-widget-style-for-614-27-1-0\" ><div\n\t\t\t\n\t\t\tclass=\"so-widget-sow-editor so-widget-sow-editor-base\"\n\t\t\t\n\t\t>\n<div class=\"siteorigin-widget-tinymce textwidget\">\n\t<p style=\"font-size: 12px;\"><strong>Abstract:<\/strong> \"<em>The aim of this study was to test the ability of a previous published model describing the sorption properties of complex solids (Bt soil horizon, sediment) under static conditions (batch mode) to describe sorption data obtained under dynamic conditions. This model assumes that the sorption properties of the multicomponent solid can be described by those of smectites present in the mineralogical assemblage. In our case, the reference smectite is a Wyoming montmorillonite. To test the model, experimental breakthrough curves of some major cations were obtained using a Bt soil horizon in different physico-chemical conditions. The fairly good agreement between the different experimental data sets and predicted breakthrough curves demonstrates that our proposed model can be used to accurately predict ion exchange reactions occurring under dynamic conditions between Na<sup>+<\/sup>, Ca<sup>2+<\/sup>, and H<sup>+<\/sup> cations in a complex mineralogical assemblage. In addition, this model is also able to accurately predict previously published experimental data obtained with another B soil horizons and using Na+, Ca2+, and Mg2+ as cations. Other models reported from the literature, based either on sorption properties of pure smectites or of complex assemblages, are not able to accurately interpret experimental data proposed in this study motivating our purpose to propose another model. Therefore, our predicted model represents an alternative to models based on the generalized composite approach, which describes the reactivity of a complex material using generic sorption sites for which reactivity is not explicitly related to the properties of the individual phases of the complex material.<\/em>\" (https:\/\/doi.org\/10.1016\/j.apgeochem.2013.12.009)<\/p>\n<\/div>\n<\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-28\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 50px\" ><div id=\"pgc-614-28-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-28-0-0\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce panel-first-child panel-last-child\" data-index=\"53\" ><div style=\"padding: 25px 25px 25px 25px;\" class=\"panel-widget-style panel-widget-style-for-614-28-0-0\" ><div class=\"textwidget\"><h2 style=\"text-align: center;\"><span class=\"VIiyi\" lang=\"en\"><span class=\"JLqJ4b ChMk0b\"><span class=\"Q4iAWc\">2013: Publications about fraction collectors &amp; autosamplers<\/span><\/span><\/span><\/h2>\n<\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-29\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 0px\" ><div id=\"pgc-614-29-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-29-0-0\" class=\"so-panel widget widget_sow-editor panel-first-child panel-last-child\" data-index=\"54\" ><div style=\"padding: 0px 0px 0px 0px;\" class=\"panel-widget-style panel-widget-style-for-614-29-0-0\" ><div\n\t\t\t\n\t\t\tclass=\"so-widget-sow-editor so-widget-sow-editor-base\"\n\t\t\t\n\t\t><h3 class=\"widget-title\">Effluent collected by LAMBDA OMNICOLL fraction collector from the glass column filled with Bt horizon of a natural soil and analyzed by ion chromatography to study the sorption of major cations (Ca, Na) on a natural sediment<\/h3>\n<div class=\"siteorigin-widget-tinymce textwidget\">\n\t<\/div>\n<\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-30\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 50px\" ><div id=\"pgc-614-30-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-30-0-0\" class=\"so-panel widget widget_sow-editor panel-first-child panel-last-child\" data-index=\"55\" ><div\n\t\t\t\n\t\t\tclass=\"so-widget-sow-editor so-widget-sow-editor-base\"\n\t\t\t\n\t\t>\n<div class=\"siteorigin-widget-tinymce textwidget\">\n\t<p>Lu, J., Beaucaire, C., &amp; Tertre, E. (2013).\u00a0 <strong>Predictive model for migration of metallic cations in natural sediments.<\/strong> Procedia Earth and Planetary Science 7 ( 2013 ) 529 \u2013 532.<br \/>\nCEA, DANS\/DPC\/SECR\/L3MR and Universit\u00e9 de Poitiers-CNRS, France.<br \/>\n<a href=\"https:\/\/doi.org\/10.1016\/j.proeps.2013.03.059\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.1016\/j.proeps.2013.03.059<\/a><\/p>\n<p>&nbsp;<\/p>\n<div id=\"attachment_1853\" style=\"width: 428px\" class=\"wp-caption alignnone\"><img aria-describedby=\"caption-attachment-1853\" loading=\"lazy\" decoding=\"async\" class=\"wp-image-1853 size-medium\" src=\"https:\/\/www.fractioncollector.info\/wp-content\/uploads\/Effluent-was-collected-by-OMNICOLL-fraction-collector-from-the-glass-column-chromatography-with-Bt-horizon-418x181.png\" alt=\"Effluent was collected by OMNICOLL fraction collector from the glass column chromatography with Bt horizon\" width=\"418\" height=\"181\" srcset=\"https:\/\/www.fractioncollector.info\/wp-content\/uploads\/Effluent-was-collected-by-OMNICOLL-fraction-collector-from-the-glass-column-chromatography-with-Bt-horizon-418x181.png 418w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/Effluent-was-collected-by-OMNICOLL-fraction-collector-from-the-glass-column-chromatography-with-Bt-horizon-150x65.png 150w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/Effluent-was-collected-by-OMNICOLL-fraction-collector-from-the-glass-column-chromatography-with-Bt-horizon-768x333.png 768w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/Effluent-was-collected-by-OMNICOLL-fraction-collector-from-the-glass-column-chromatography-with-Bt-horizon.png 809w\" sizes=\"auto, (max-width: 418px) 100vw, 418px\" \/><p id=\"caption-attachment-1853\" class=\"wp-caption-text\">https:\/\/doi.org\/10.1016\/j.proeps.2013.03.059<\/p><\/div>\n<\/div>\n<\/div><\/div><\/div><div id=\"pgc-614-30-1\"  class=\"panel-grid-cell\" ><div id=\"panel-614-30-1-0\" class=\"so-panel widget widget_sow-editor panel-first-child panel-last-child\" data-index=\"56\" ><div style=\"padding: 0px 0px 30px 10px;\" class=\"panel-widget-style panel-widget-style-for-614-30-1-0\" ><div\n\t\t\t\n\t\t\tclass=\"so-widget-sow-editor so-widget-sow-editor-base\"\n\t\t\t\n\t\t>\n<div class=\"siteorigin-widget-tinymce textwidget\">\n\t<p style=\"font-size: 14px;\"><strong>Abstract:<\/strong> \"<em>Recently, a sorption model based on ion exchange equilibria was proposed and successfully applied to predict the sorption behavior of metallic cations in natural sediments under batch conditions [1]. In the present study, this sorption model is coupled with a 1-D transport simulation code to check its validity under dynamic conditions. Therefore, reactive transport experiments of major cations (Ca, Na) using a natural sediment column were studied in the laboratory. A comparison between experimental and predicted breakthrough curves is reported. Results show that the sorption model coupled with the transport code is able to predict with good confidence the migration of major cations in a natural sediment. The participation of protons in the ion exchange process was confirmed by the variation of the experimental pH, coinciding with the model's prediction.\" <\/em>(https:\/\/doi.org\/10.1016\/j.proeps.2013.03.059)<em><br \/>\n<\/em><\/p>\n<\/div>\n<\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-31\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 50px\" ><div id=\"pgc-614-31-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-31-0-0\" class=\"so-panel widget widget_black-studio-tinymce widget_black_studio_tinymce panel-first-child panel-last-child\" data-index=\"57\" ><div style=\"padding: 25px 25px 25px 25px;\" class=\"panel-widget-style panel-widget-style-for-614-31-0-0\" ><div class=\"textwidget\"><h2 style=\"text-align: center;\"><span class=\"VIiyi\" lang=\"en\"><span class=\"JLqJ4b ChMk0b\"><span class=\"Q4iAWc\">2012 &amp; earlier: Publications about fraction collectors &amp; autosamplers<\/span><\/span><\/span><\/h2>\n<\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-32\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 0px\" ><div id=\"pgc-614-32-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-32-0-0\" class=\"so-panel widget widget_sow-editor panel-first-child panel-last-child\" data-index=\"58\" ><div style=\"padding: 0px 0px 0px 0px;\" class=\"panel-widget-style panel-widget-style-for-614-32-0-0\" ><div\n\t\t\t\n\t\t\tclass=\"so-widget-sow-editor so-widget-sow-editor-base\"\n\t\t\t\n\t\t><h3 class=\"widget-title\">LAMBDA OMNICOLL fraction collector was used to collect the elute in 1.2 \u2212 3.6 mL fractions from the contaminated sediments packed column to investigate the mobilization of Tc under fully saturated seawater flow conditions<\/h3>\n<div class=\"siteorigin-widget-tinymce textwidget\">\n\t<\/div>\n<\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-33\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 50px\" ><div id=\"pgc-614-33-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-33-0-0\" class=\"so-panel widget widget_sow-editor panel-first-child panel-last-child\" data-index=\"59\" ><div\n\t\t\t\n\t\t\tclass=\"so-widget-sow-editor so-widget-sow-editor-base\"\n\t\t\t\n\t\t>\n<div class=\"siteorigin-widget-tinymce textwidget\">\n\t<p>Eagling, J. (2012). <strong>The effect of sea level rise on radionuclide mobility at contaminated nuclear sites<\/strong> (Doctoral dissertation, University of Plymouth).<br \/>\n<a class=\"waffle-rich-text-link\" href=\"https:\/\/dx.doi.org\/10.24382\/3421\" target=\"_blank\" rel=\"noopener\">https:\/\/dx.doi.org\/10.24382\/3421<\/a><\/p>\n<p><strong>Keywords:<\/strong>\u00a0Column, HPLC, Fe-reducing sediments, Tc, polyetheretherketone (PEEK) self-pack column, Eh, Sediment reoxidation<\/p>\n<\/div>\n<\/div><\/div><\/div><div id=\"pgc-614-33-1\"  class=\"panel-grid-cell\" ><div id=\"panel-614-33-1-0\" class=\"so-panel widget widget_sow-editor panel-first-child panel-last-child\" data-index=\"60\" ><div style=\"padding: 0px 0px 30px 10px;\" class=\"panel-widget-style panel-widget-style-for-614-33-1-0\" ><div\n\t\t\t\n\t\t\tclass=\"so-widget-sow-editor so-widget-sow-editor-base\"\n\t\t\t\n\t\t>\n<div class=\"siteorigin-widget-tinymce textwidget\">\n\t<p style=\"font-size: 12px;\"><strong>Abstract:<\/strong> <em>\"Predicted sea level rise would increase the vulnerability of low lying coastal legacy nuclear sites to inundation and intrusion with oxygenated seawater. This could have a significant impact on the mobility of redox-sensitive radionuclides such as Tc. Here, batch and column experiments were used to simulate and investigate the effect of these processes on the mobilization of Tc from sediments under a range of geochemically reduced conditions. Batch experiments showed that only a small proportion of Tc was rapidly (within 5 days) released from the sediments into seawater and groundwater. The subsequent Tc release was slowest and ultimately limited to the greatest extent (17%) in initially Fe-reducing sediments, when they were reoxidized in seawater. Thus, the cycling of iron and the impact of the water chemistry on iron mineralogy were important for hindering Tc release. Column experiments showed that iron minerals were less effective at retarding Tc release under flow-through conditions. Kinetically controlled and solubility limited Fe dissolution led to ongoing Tc release from the sediments; i.e. the retarding effect of iron phases was temporary, and significantly more Tc was mobilized (79\u201393%) compared with the batch experiments (17\u201345%). These results demonstrate the potential for Tc(IV) to be oxidized and mobilized from sediments at coastal nuclear sites resulting from predicted intrusion and inundation with oxic seawater.\" <\/em>(https:\/\/doi.org\/10.1021\/es3025935)<em><br \/>\n<\/em><\/p>\n<\/div>\n<\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-34\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 0px\" ><div id=\"pgc-614-34-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-34-0-0\" class=\"so-panel widget widget_sow-editor panel-first-child panel-last-child\" data-index=\"61\" ><div style=\"padding: 0px 0px 0px 0px;\" class=\"panel-widget-style panel-widget-style-for-614-34-0-0\" ><div\n\t\t\t\n\t\t\tclass=\"so-widget-sow-editor so-widget-sow-editor-base\"\n\t\t\t\n\t\t><h3 class=\"widget-title\">LAMBDA OMNICOLL fraction collector was used to collect the eluent from the contaminated sediment packed PEEK column to determine the pH and 90Sr by liquid scintillation<\/h3>\n<div class=\"siteorigin-widget-tinymce textwidget\">\n\t<\/div>\n<\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-35\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 50px\" ><div id=\"pgc-614-35-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-35-0-0\" class=\"so-panel widget widget_sow-editor panel-first-child panel-last-child\" data-index=\"62\" ><div\n\t\t\t\n\t\t\tclass=\"so-widget-sow-editor so-widget-sow-editor-base\"\n\t\t\t\n\t\t>\n<div class=\"siteorigin-widget-tinymce textwidget\">\n\t<p>Eagling, J. (2012) <strong>The effect of sea level rise on radionuclide mobility at contaminated nuclear sites.<\/strong><br \/>\nPlymouth University, UK<br \/>\n<a href=\"https:\/\/pearl.plymouth.ac.uk\/handle\/10026.1\/1248\" target=\"_blank\" rel=\"noopener\">https:\/\/pearl.plymouth.ac.uk\/handle\/10026.1\/1248<\/a> (2013 Oct. 13)<\/p>\n<p><strong>Keywords:<\/strong> contaminated land, porewater salinization, radionuclide, geochemistry, release kinetics, transport, oxic and reduced sediments<\/p>\n<div id=\"attachment_1856\" style=\"width: 331px\" class=\"wp-caption alignnone\"><img aria-describedby=\"caption-attachment-1856\" loading=\"lazy\" decoding=\"async\" class=\"wp-image-1856 size-medium\" src=\"https:\/\/www.fractioncollector.info\/wp-content\/uploads\/OMNICOLL-fraction-collector-for-collecting-eluent-from-radionuclide-contaminated-sediment-packed-PEEK-column-321x278.png\" alt=\"\" width=\"321\" height=\"278\" srcset=\"https:\/\/www.fractioncollector.info\/wp-content\/uploads\/OMNICOLL-fraction-collector-for-collecting-eluent-from-radionuclide-contaminated-sediment-packed-PEEK-column-321x278.png 321w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/OMNICOLL-fraction-collector-for-collecting-eluent-from-radionuclide-contaminated-sediment-packed-PEEK-column-150x130.png 150w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/OMNICOLL-fraction-collector-for-collecting-eluent-from-radionuclide-contaminated-sediment-packed-PEEK-column-768x665.png 768w, https:\/\/www.fractioncollector.info\/wp-content\/uploads\/OMNICOLL-fraction-collector-for-collecting-eluent-from-radionuclide-contaminated-sediment-packed-PEEK-column.png 769w\" sizes=\"auto, (max-width: 321px) 100vw, 321px\" \/><p id=\"caption-attachment-1856\" class=\"wp-caption-text\">https:\/\/pearl.plymouth.ac.uk\/handle\/10026.1\/1248 (2013 Oct. 13)<\/p><\/div>\n<\/div>\n<\/div><\/div><\/div><div id=\"pgc-614-35-1\"  class=\"panel-grid-cell\" ><div id=\"panel-614-35-1-0\" class=\"so-panel widget widget_sow-editor panel-first-child panel-last-child\" data-index=\"63\" ><div style=\"padding: 0px 0px 30px 10px;\" class=\"panel-widget-style panel-widget-style-for-614-35-1-0\" ><div\n\t\t\t\n\t\t\tclass=\"so-widget-sow-editor so-widget-sow-editor-base\"\n\t\t\t\n\t\t>\n<div class=\"siteorigin-widget-tinymce textwidget\">\n\t<p style=\"font-size: 12px;\"><strong>Abstract:<\/strong> <em>\"Global sea levels are expected to rise as a result of climate change, which will lead to the inundation and erosion of low lying coastal areas and accelerate the intrusion of seawater into sub-surface sediments. Many of the UK\u2019s legacy nuclear facilities are located in close proximity to the shore, raising questions regarding the potential mobilisation of radionuclides during sea level rise. Here batch and column experiments were used to simulate and investigate the effect of these processes on the mobilisation of key radionuclides Tc, 90Sr and U from oxic and reduced sediments under sea level rise scenarios. Strontium-90 was rapidly mobilised from exchangeable surface sites from oxic sediments during inundation and erosion scenarios with seawater (\u2248 60%). Strontium release was driven by ion exchange between Sr90 and Mg2+ cations present in high concentrations in seawater. Uranium release from oxic and reduced sediments was kinetically controlled, characterised by slow release from a range of binding sites, promoted by the formation of U-carbonate complexes. Uranium mobilisation was slower from reduced sediments compared with oxic sediments under seawater flow conditions; therefore reduced sediments would act as a longer term source of U to marine environments. Release was more extensive from initially nitrate reducing sediments (53%) compared with extensively iron reducing sediments (38%), with the difference in release explained by the longer contact period of U(VI) with the iron reducing sediment relative to the nitrate reducing sediment which would lead to slower desorption.\" <\/em>(https:\/\/pearl.plymouth.ac.uk\/handle\/10026.1\/1248 (2013 Oct. 13))<em><br \/>\n<\/em><\/p>\n<\/div>\n<\/div><\/div><\/div><\/div><\/div><div id=\"pg-614-36\"  class=\"panel-grid panel-no-style\"  style=\"margin-bottom: 50px\" ><div id=\"pgc-614-36-0\"  class=\"panel-grid-cell\" ><div id=\"panel-614-36-0-0\" class=\"so-panel widget widget_sow-editor panel-first-child panel-last-child\" data-index=\"64\" ><div style=\"padding: 0px 0px 0px 0px;\" class=\"panel-widget-style panel-widget-style-for-614-36-0-0\" ><div\n\t\t\t\n\t\t\tclass=\"so-widget-sow-editor so-widget-sow-editor-base\"\n\t\t\t\n\t\t>\n<div class=\"siteorigin-widget-tinymce textwidget\">\n\t<h3><strong>Eluate was collected (60 min per fraction) by means of a LAMBDA OMNICOLL fraction collector to determine the silver ion release from coated catheters<\/strong><\/h3>\n<p>Aylvin Jorge Angelo Athanasius Dias, Edith Elisabeth M. Van Den Bosch, Astrid Franken (2010). <strong>Antimicrobial coating.<\/strong> US Patent no. US 2010\/0113871 A1.<br \/>\n<a href=\"https:\/\/patents.google.com\/patent\/US20100113871\" target=\"_blank\" rel=\"noopener\">https:\/\/patents.google.com\/patent\/US20100113871<\/a> (2022 Oct. 12)<\/p>\n<\/div>\n<\/div><\/div><\/div><\/div><\/div><\/div>","protected":false},"excerpt":{"rendered":"<p>Short selection of references for fraction collector and automatic sampler OMNICOLL.<\/p>","protected":false},"author":2,"featured_media":1311,"parent":0,"menu_order":0,"comment_status":"closed","ping_status":"closed","template":"templates\/template-full-notitle.php","meta":{"footnotes":""},"class_list":["post-614","page","type-page","status-publish","has-post-thumbnail","hentry","post","post-with-thumbnail","post-with-thumbnail-icon"],"yoast_head":"<!-- This site is optimized with the Yoast SEO plugin v27.6 - https:\/\/yoast.com\/product\/yoast-seo-wordpress\/ -->\n<title>Publications about fraction collectors &amp; autosamplers as references for LAMBDA OMNICOLL &#8211; LAMBDA OMNICOLL | LAMBDA Laboratory Instruments<\/title>\n<meta name=\"description\" content=\"The best references for fraction collectors &amp; 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