Academic literature on the topic 'In-situ electrokinetics'
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Journal articles on the topic "In-situ electrokinetics"
Lukman, Salihu, Mohammed Hussain Essa, Nuhu Dalhat Mu'azu, and Alaadin Bukhari. "Coupled Electrokinetics-Adsorption Technique for Simultaneous Removal of Heavy Metals and Organics from Saline-Sodic Soil." Scientific World Journal 2013 (2013): 1–9. http://dx.doi.org/10.1155/2013/346910.
Full textMohamedelhassan, E., and J. Q. Shang. "Electrokinetics-generated pore fluid and ionic transport in an offshore calcareous soil." Canadian Geotechnical Journal 40, no. 6 (December 1, 2003): 1185–99. http://dx.doi.org/10.1139/t03-060.
Full textLi, Shanshan, Yukun Ren, Haochen Cui, Quan Yuan, Jie Wu, Shigetoshi Eda, and Hongyuan Jiang. "Alternating current electrokinetics enhanced in situ capacitive immunoassay." ELECTROPHORESIS 36, no. 3 (November 29, 2014): 471–74. http://dx.doi.org/10.1002/elps.201400284.
Full textSafdar, Muhammad Umair, Maria Mavroulidou, Michael J. Gunn, Christopher Gray, Diane Purchase, Jonathan Garelick, and Ian Payne. "Implementation of biocementation for a partially saturated problematic soil of the UK railway network." E3S Web of Conferences 195 (2020): 05006. http://dx.doi.org/10.1051/e3sconf/202019505006.
Full textChew, Chin F., and Tian C. Zhang. "In-situ remediation of nitrate-contaminated ground water by electrokinetics/iron wall processes." Water Science and Technology 38, no. 7 (October 1, 1998): 135–42. http://dx.doi.org/10.2166/wst.1998.0286.
Full textChoi, Eunpyo, Kilsung Kwon, Daejoong Kim, and Jungyul Park. "An electrokinetic study on tunable 3D nanochannel networks constructed by spatially controlled nanoparticle assembly." Lab on a Chip 15, no. 2 (2015): 512–23. http://dx.doi.org/10.1039/c4lc00949e.
Full textAhualli, Silvia, Sara Bermúdez, Félix Carrique, María L. Jiménez, and Ángel V. Delgado. "AC Electrokinetics of Salt-Free Multilayered Polymer-Grafted Particles." Polymers 12, no. 9 (September 15, 2020): 2097. http://dx.doi.org/10.3390/polym12092097.
Full textLarsen, Mads S., Murat N. Yesibolati, and Kristian S. Mølhave. "In-situ Electrokinetics Using Liquid Phase Transmission Electron Microscopy." Microscopy and Microanalysis 28, S1 (July 22, 2022): 1908–10. http://dx.doi.org/10.1017/s1431927622007474.
Full textLarsen, Mads S., Murat N. Yesibolati, and Kristian S. Mølhave. "In-situ Electrokinetics Using Liquid Phase Transmission Electron Microscopy." Microscopy and Microanalysis 27, S2 (November 2021): 95–96. http://dx.doi.org/10.1017/s1431927621013477.
Full textYeung, Albert T., and Subbaraju Datla. "Fundamental formulation of electrokinetic extraction of contaminants from soil." Canadian Geotechnical Journal 32, no. 4 (August 1, 1995): 569–83. http://dx.doi.org/10.1139/t95-060.
Full textDissertations / Theses on the topic "In-situ electrokinetics"
Boeva, Valentina. "Distribution of ammonium nitrate as nitrogen-containing nutrient for in situ biodegradation by means of electrokinetics." Thesis, National Library of Canada = Bibliothèque nationale du Canada, 1995. http://www.collectionscanada.ca/obj/s4/f2/dsk3/ftp04/MQ44874.pdf.
Full textLoulergue, Patrick. "Caractérisation In-Situ de dépôts formés en filtration membranaire de suspensions particulaires et de biofluides : intéraction entre structure locale et performances du procédé." Thesis, Toulouse, INSA, 2012. http://www.theses.fr/2012ISAT0046/document.
Full textMembrane fouling is one of the major drawbacks of membrane bioreactors. This study is thus a contribution to the understanding of the dynamic structuring of complex deposits build-up during dead-end filtration of complex biofluids. Several tools were used to perform in-situ characterization of cake layer structural properties at local scale and to link them to global filtration performances. The electrokinetics properties of the deposit were also investigated. An optical and an acoustic method were used to measure local cake thickness and growth kinetics. The thicknesses given by the two methods were first compared. It was shown that for compact deposits the two different methods lead to the same thickness of the deposit. For more porous deposits, these two methods allow to obtain complementary data at two different depths of the deposits. The influence of operating conditions on cake layer structuring during filtration of modelled particles was evaluated. Using the optical method it was shown that, whatever the operating conditions, the cake structure is not constant in time. Furthermore, a spatial variability of the cake layer thickness might exist especially in the case of weak particle-particle repulsion. Finally, it has been investigated whether the different methods could be applied or not to the case of biofluid filtration. The structural properties of the complex deposits built up during diluted activated sludge filtration were investigated. Cake compressibility was observed at global scale by a monitoring of process performances and was also observed at local scale: cake thickness decreases as TMP increases. Furthermore, at local scale, a spatial variability of deposit structure was found. Particle addition into the biofluid was assessed in order to mitigate compressibility effects
Sin, Lai Yi Mandy. "IN SITU ELECTROKINETIC SAMPLE PREPARATION FOR SELF-ASSEMBLED MONOLAYER BASED ELECTROCHEMICAL BIOSENSING." Diss., The University of Arizona, 2011. http://hdl.handle.net/10150/205176.
Full textYang, Kai. "In Situ Preconcentration by AC Electrokinetics for Rapid and Sensitive Nanoparticle Detection." 2011. http://trace.tennessee.edu/utk_graddiss/1146.
Full textShen, Po-Cheng, and 沈柏丞. "Study On In-Situ Treatment of Lead Contaminated Soils by The Pilot-scale Electrokinetics." Thesis, 2012. http://ndltd.ncl.edu.tw/handle/24072067069012152120.
Full text朝陽科技大學
環境工程與管理系碩士班
100
The purpose of this study is to discuss the removal efficiency of heavy metal pollutants in the soil and economic cost by the in-situ pilot-scale electrokinetics. First, it will proceed the removal efficiency experiment of lead form the in-situ soil by the small pilot-scale electrokinetics in laboratory. It is to understand the electrochemical phenomenons of the electro-osmosis flow, ion migration and electrolysis effectiveness etc. Second, it will proceed the in-situ experiment in taichung and nantou that the operating parameters include: system electrolyte (0.01M EDTA-2Na, 0.01M Na2CO3), electrode material (Anode: graphite plate, Cathode: stainless steel plate), the voltage gradient, constant current and constant voltage are 1 V cm-1, 10A and 80V, respectively. In the remediation process, it will be analysis and monitoring that (1) the pH and conductivity values and lead concentration of the system electrolyte, (2) the pH and conductivity values and lead concentration of the soil, (3) current, voltage, temperature and fertility test (Ca、Mg、K、Na、F、Mn、Cu、Zn、P、OM、CEC). All of them to understand the removal efficiency of lead in the in-situ soil by electrokinetics and to count the power consumption costs. Form the experimental results show, passed through 56 days treatment, the mean concentration of lead in the soil was from 7190 mg Kg-1 to 2050 mg Kg-1 in wuri site. The removal efficiency is around 72%. In nantou site, the mean concentration of lead in the soil was from 7246 mg Kg-1 to 6647 mg Kg-1 that removal efficiency about 10% by 14 days treatment. In addition, the soil not happened the acidification in the electrokinetics with the 0.01M Na2CO3 and 0.01M EDTA operated. In the aspect of tlhe operating costs that example of the wuri site. The 1% removal efficiency of lead per 1.0 m2 is around NT. 8.82 dollars. It needs NT. 12.6 dollars to remove 100 mg Kg-1 Pb.
Lai, Yung-Chang, and 賴詠章. "Investigation of effectiveness and factors on in-situ electrokinetics (CEEK) for treating pb contaminated soils." Thesis, 2013. http://ndltd.ncl.edu.tw/handle/33640120486544987889.
Full text朝陽科技大學
環境工程與管理系碩士班
101
This study is to investigate the critical effects about circulation-enhanced electrokinetics (CEEK) in near-real scale to remediate the Pb contaminated soils in Nantou city. Through this study, the lead removal efficiency and cost effectiveness of CEEK in near-real scale can be obtained. The experimental parameters were controlled as: operation solution (0.01 M EDTA-2Na, 0.01 M Na2CO3); electrode (anode: graphite, cathode: stainless steel); voltage gradient 1 V cm-1. After 63-day CEEK treatment, the Pb removal efficiency was around 64% and the average Pb concentration was decreased from 7,246 mg/Kg down to 2,612 mg/Kg. The operational cost of electricity of removing 1% lead was around 9.84 NT dollars based on one square meters of polluted soil. This result is similar to our previous study in pilot scale (8.82 NT dollars). Under CEEK operation in near-real scale, the pH and conductivity of the treated soils was maintained at neutral and stable situation, respectively. In addition, the current, voltage, and temperature of CEEK system could be controlled at the stable status as well. The fertilization of the CEEK treated soil was slightly decreased. The fertilizer with Ca and P should be added in the CEEK treated soils.
Hsueh, Wei Chen, and 薛威震. "A Study on In-situ Treatment of Pb/Cu Contaminated Soils by Electrokinetics and a Reactive Wall of Cation Exchange Resin." Thesis, 1999. http://ndltd.ncl.edu.tw/handle/90833627768180797350.
Full text國立中山大學
環境工程研究所
87
In order to increase the in-situ remediation efficiency of the contaminated soils by electrokinetics, this study combines the electrokinetic remediation technology and the reactive wall of cation exchange resin and changes the cathode reservoir solution every 5 or 10 days. Experimental results have shown that this soil treatment technology is capable of increasing the remediation efficiency of the heavy metals Cu and Pb up to 86.54% and 61.12%. After the soil remediation, the cation exchange resin could be regenerated and reused. In so doing, nearly 80% Cu and 50% Pb caught by the resin could be recovered. The following experimental factors are studied to determine their effects on the remediation efficiency: (1)soil type, (2)the kind of cathode and anode reservoir solutions, (3)the frequency of changing cathode reservoir solution, (4)the frequency of changing the reactive wall of the cation exchange resin, and(5)the initial concentration of Cu or Pb. The experimental data obtained are analyzed statistically to determine the contribution of each factor. For Cu removal, the kind of the reservoir solution is the most influencing factor, and the frequency of changing reservoir solution is the second. For Pb removal, no significant factor can be fond. Accordingly, under appropriate operating conditions, the new treatment train technology used in this study could effectively enhance the remediation efficiency by electrokinetics alone.
Chyi-Yech, Liu, and 劉奇岳. "A Study on Optimal Operating Conditions for In-Situ Treatment of TCE and 4-CP Contaminated Soils by Electrokinetics-Fenton Process." Thesis, 1999. http://ndltd.ncl.edu.tw/handle/28259693647956276582.
Full text國立中山大學
環境工程研究所
87
This research was to determine the optimal operating conditions for in-situ treatment of trichloroethylene and 4-chlorophenol contaminated soils by electrokinetics-Fenton process. An electric gradient of 1 V/cm, deionized water in the cathode reservoir, and a reaction time of ten days were employed in all experiments. Soil types (No. 1 and No. 2), contaminant kinds (trichloroethylene and 4-chlorophenol), catalyst types (iron powder and FeSO4), catalyst dosage and position (one layer of 1.5 g iron powder placed in the soil column at a distance of 5 cm from the anode reservoir and two layer of iron powder placed in the soil column one at a distance of 5 cm from the anode reservoir and the other next to the cathode reservoir), and electrode types (graphite and stainless steel) were employed as the experimental factors in this study. In this study, treating the soil with a higher electrical conductivity would consume more H2O2 because H2O2 electrolyzed in the anode reservoir; whereas treating the soil with a higher organic content would lower the treatment efficiency because of the adsorption of contaminants and the consumption of hydroxyl radicals by the organic matter of soil. The directions of all electroosmotic flows were found to be from anode toward cathode in this investigation. Experimental results showed that the type of catalyst and its dosage affected the reaction mechanisms (i.e., "destruction" and "removal") and the treatment efficiency. For iron powder of a smaller size, the overall destruction and removal efficiency (DRE) was lower, but the percent of destruction was higher. For iron powder of a higher dosage, the DRE was lower, but the percent of destruction was higher. When trichloro-ethylene was the target pollutant, the highest destruction and removal efficiency (i.e., 88.91%) for Soil No. 1 was obtained by adding 1.5g of UPF-030 iron powder; whereas the highest destruction efficiency (i.e., 59.41%) was obtained by adding two layers of 1.5g scrap iron powder. However the highest removal efficiency (i.e., 63.64%) was obtained for Soil No. 1 by using 0.0196 M FeSO4 as the catalyst. When 4-Chlorophenol was the target pollutant, adding 1.5g of UPF-030 iron powder would yield the highest destruction and removal efficiency (i.e., 88.91%) and the highest removal efficiency (i.e., 49.84%) for Soil No. 1. But the highest destruction efficiency (i.e., 64.47%) for Soil No. 1 was obtained by adding two layers of 1.5g UPF-030 iron powder as the catalyst. For Soil No. 2 contaminated by trichloroethylene or 4-chlorophenol, a greater DRE and removal efficiency were obtained by adding one layer of 1.5 g UPF-030 iron powder. However, to obtain greater destruction efficiencies for Soil No. 2 contaminated by trichloroethylene and 4-Chlorophenol, adding one layer of scrap and UPF-150 iron powder, respectively are necessary.
Chun-KaiChiang and 姜竣凱. "AC Electrokinetic Manipulation for Separation and in situ Detection of Cancer Cells." Thesis, 2014. http://ndltd.ncl.edu.tw/handle/k48g9b.
Full text國立成功大學
生物醫學工程學系
102
Recently, personalized cancer treatment had been developed vigorously. However, there are many problems in traditional isolation and detection methods, such as low purity, complicated operation procedures, and expensive instruments. Thus, how to separate tumor cells from clinical samples rapidly and precisely and how to improve the efficient diagnosis for a proper reference of personalized treatment are the aims of this study. AC electrokinetics for the manipulation of cells had been widely integrated into microfluidic chips and biosensors for manipulating and analyzing specific targets accurately. In this study, dielectrophoresis and electrorotation were integrated into our novel biochip platform to achieve separation of tumor cells, capture of single tumor cell and analysis of drug response in the tumor cell at the same reaction. In this thesis, three subjects will be introduced, (1) Separation of cancer cells from complex samples by electrokinetics: We developed a new on-chip separation method by different dielectric properties, cancer cells were transported to specific detection area and non-cancer cells were excluded out of detection area as an AC electric field was applied to each electrodes. (2) Capture of single cancer cell by a switch circuit and three-dimensional dielectrophoresis: When single cancer cell entered into detection area, the upper electrodes were turned on and generated a strong electric field with under electrodes to block extra cancer cells. That single cell would be tracked to the detection center with a relatively low electric field. The efficiency to capture single cell is up to 85% within one min. (3) Assessment of cancer cells’ electrical characteristics by spectrum of three-dimensional electrorotation (ROT): The results of ROT spectrum can be achieved rapid assessment of cancer cells’ electrical characteristic, in which the variations can be reduced obviously and the high frequency of spectrum can be analyzed more completely than traditional ROT method by combining an extra-stabilized system into our device. As a result, the optimal frequency for electrorotation discrimination of cancer cell was found at 100 kHz and the total detection time is within 5 min per cell. Finally, we developed a miniaturized and integrated biochip that can be used in samples pretreatment and detection of cancer cells successively. We hope this platform can be used widely in personalized cancer treatment because of its convenient, timesaving and low cost.
Liu, Shou-Heng, and 劉守恒. "In-situ Speciation Studies of Copper in Contaminated Soils and Sludges during Electrokinetic Remediation." Thesis, 2004. http://ndltd.ncl.edu.tw/handle/76376579591536515459.
Full text國立成功大學
環境工程學系碩博士班
92
Electrokinetic remediation (EKR) has been becoming one of the most feasible technologies for in-situ soil decontamination. However, the complex transport phenomena, electrochemistry and complexation reaction paths involved in the EKR is still not well understood. Thus, the main objective of this work was to study the speciation of copper in heavy copper contaminated soils during EKR by EXAFS, XANES, solid-state NMR (SSNMR), FTIR, electron paramagnetic resonance (EPR) and X-ray photoelectron spectroscopy (XPS). An in-situ EXAFS cell was used to reveal the possible reaction pathway during EKR. In addition, EKR of sludges was also conducted to extend the applications. In simplified soil EKR systems (SiO2 or Al2O3), by XANES, it was found that the main copper species on SiO2 and Al2O3 were outer-sphere complexes (aqueous Cu(II)) (80%) and inner-sphere complexes (Cu/Al2O3) (59%), respectively. The mobility of copper in the Al2O3 matrix during EKR was less than that in the SiO2 system possibly because of the strong bonding between copper and Al2O3 surfaces with the edge-sharing bidentate mode (inner-sphere complexes). It was found that about 54% and 27% of Cu(II) on SiO2 and Al2O3, respectively were migrated to the cathode under the electric field (5 V/cm) for 180 min. Speciation of copper-humic substances (HS) in the EKR of the contaminated soil was also studied by in-situ EXAFS and XANES spectroscopies. The least-square fits of the XANES spectra suggested that the main copper species in the contaminated soil were Cu-HS (50%), CuCO3 (28%), Cu2O (11%) and CuO (11%). By FTIR, Cu-HS as an unidentate complex was observed. The Cu-HS in the contaminated soil possessed equatorial and axial Cu-O bond distances of 1.94 and 2.17 Å with coordination numbers (CNs) of 3.6 and 1.4, respectively. In the EKR process, the axial Cu-O bond distance in the Cu-HS complexes was increased by 0.15 Å, which might be due to a ligand exchange of the Cu-HS with H2O molecules in the electrolyte. After 180 min of EKR, about 50% of the Cu-HS complexes (or 24% of total copper) in the soil were dissolved and formed [Cu(H2O)6]2+ in the electrolyte and 71% (or 17% of total copper in the soil) of which were migrated to the cathode under the electric field (5 V/cm). In the ethylenediaminetetraacetic acid (EDTA)-enhanced EKR of soils, the main copper species in the contaminated soil were CuCO3 (41%), CuO (40%) and adsorbed copper (Cu/SiO2) (19%). The fitted EXAFS data showed that the bond distance of Cu-(O)-Si was 3.25 Å with a coordination number (CN) of 1.0 in the second shells, suggesting a chemical interaction between copper and the soil surfaces. In the presence of EDTA (0.05 M), a Cu-EDTA complex having the equatorial and axial Cu-O bond distances of 1.96 Å and 2.21 Å, respectively, was observed. The EPR spectra showed that copper (Cu(II)) was complexed with EDTA in a square-plannar arrangement with four oxygen-containing groups. Interestingly, after 180 min of EKR, the axial Cu-O bond distance was increased by 0.1 Å. The perturbation might be attributed to the possibility that the weak-field carboxylic acid groups of EDTA in the equatorial plane of Cu(II) were replaced by the strong-field water molecules. In the EKR of a CMP sludge, the main copper species in the sludge were Cu(OH)2 (73%), nano CuO (14%) and CuO (13%). About 85% of the copper were dissolved (possibly formed [Cu(H2O)6]2+) in the electrolyte and 13% of which was migrated to the cathode under the electric field (5 V/cm) for 120 min. In addition, it was found that nano CuO has a higher mobility than its bulk CuO during EKR, which may be due to at least two possibilities: (1)nano copper has a higher dissolution rate; (2) nano CuO may be migrated directly to cathode. An exploratory study for oxidation of gas-phase mercury by nitric acid vapor and halogen gas was also conducted. Arrhenius expression for the oxidation of gas phase mercury by bromine gas is 8.4×10-16 exp [-(554 ± 69)/T] cm3 molecule-1s-1, corresponding to a rate coefficient of (1.3 ± 0.3)×10-16 cm3 molecule-1s-1 at 294 K and an activation energy of 4.6 ± 0.6 kJ mol-1. The cost for 90% removal of mercury from a simulated flue gas of power plants by Br2 gas was estimated to about 5000$/lb, which is a cost-effective method compared to other technologies. In addition, the oxidation products and excess bromine gas are easy to handle since the oxidized form of mercury can subsequently be removed by the dissolution in an aqueous gas absorber or by the adsorption on sorbents in a baghouse or electrostatic precipitator.
Books on the topic "In-situ electrokinetics"
A, Parker Randy, National Risk Management Research Laboratory (U.S.), and Superfund Innovative Technology Evaluation Program (U.S.), eds. In situ bioremediation by electrokinetic injection. Cincinnati, OH: U.S. Environmental Protection Agency, [National Risk Management Research Laboratory, 2000.
Find full textSuperfund Innovative Technology Evaluation Program (U.S.), National Risk Management Research Laboratory (U.S.), and Tetra Tech EM Inc, eds. Sandia National Laboratories in situ electrokinetic extraction technology: Innovative technology evaluation report. Cincinnati, Ohio: National Risk Management Research Laboratory, Office of Research and Development, U.S. Environmental Protection Agency, 1999.
Find full textUnited States. Environmental Protection Agency., ed. DEMONSTRATION BULLETIN, IN SITU ELECTROKINETIC EXTRACTION SYSTEM... EPA/540/MR-97/509... U.S. ENVIRONMENTAL PROTECTION AGENCY... NOVEMBER 19. [S.l: s.n., 1999.
Find full textUnited States. Environmental Protection Agency, ed. DEMONSTRATION BULLETIN, IN SITU ELECTROKINETIC EXTRACTION SYSTEM... EPA/540/MR-97/509... U.S. ENVIRONMENTAL PROTECTION AGENCY... NOVEMBER 19. [S.l: s.n., 1999.
Find full textBook chapters on the topic "In-situ electrokinetics"
Shiba, S., Y. Hirata, and T. Seno. "In-situ Electrokinetic Remediation of Soil and Water in Aquifer Contaminated by Heavy Metal." In Groundwater Updates, 135–40. Tokyo: Springer Japan, 2000. http://dx.doi.org/10.1007/978-4-431-68442-8_23.
Full textKim, Soon-Oh, Keun-Young Lee, and Kyoung-Woong Kim. "Fundamentals of electrokinetics." In In-Situ Remediation of Arsenic-Contaminated Sites, 87–113. CRC Press, 2014. http://dx.doi.org/10.1201/b17619-6.
Full text"Fundamentals of electrokinetics." In In-Situ Remediation of Arsenic-Contaminated Sites, 121–48. CRC Press, 2018. http://dx.doi.org/10.1201/b17619-13.
Full text"1 In Situ Remediation of Contaminated Soils by Electrokinetic Processes." In Hazardous and Radioactive Waste Treatment Technologies Handbook, 129–66. CRC Press, 2001. http://dx.doi.org/10.1201/9781420036459-9.
Full textPavlatos, Nikiforos G., and Athanasios (Tom) Scarpas. "Framework for in situ soil stabilization based on electrokinetic principles." In Functional Pavement Design, 1247–56. CRC Press, 2016. http://dx.doi.org/10.1201/9781315643274-138.
Full textShiba, S., and Y. Hirata. "In-situ electrokinetic remediation of groundwater contaminated by heavy metal." In Computational Methods in Water Resources, Proceedings of the XIVth International Conference on Computational Methods in Water Resources (CMWR XIV), 883–90. Elsevier, 2002. http://dx.doi.org/10.1016/s0167-5648(02)80154-x.
Full textHirata, Y., S. Shiba, T. Seno, and K. Yamaberi. "In-situ electrokinetic and hydraulic remediation of saturated aquifer contaminated by heavy metal." In Groundwater Engineering - Recent Advances. Taylor & Francis, 2003. http://dx.doi.org/10.1201/9781439833605.ch39.
Full textMarks, Robert E., Yalcin B. Acar, and Robert J. Gale. "In Situ Remediation of Contaminated Soils Containing Hazardous Mixed Wastes by Bio-Electrokinetic Remediation and Other Competitive." In Remediation of Hazardous Waste Contaminated Soils, 405–36. Routledge, 2018. http://dx.doi.org/10.1201/9780203740880-18.
Full textCameselle, C. "Electrokinetic remediation and other physico-chemical remediation techniques for in situ treatment of soil from contaminated nuclear and NORM sites." In Environmental Remediation and Restoration of Contaminated Nuclear and Norm Sites, 161–84. Elsevier, 2015. http://dx.doi.org/10.1016/b978-1-78242-231-0.00008-9.
Full textConference papers on the topic "In-situ electrokinetics"
Haroun, Muhammad Raeef, Bisweswar Ghosh, George V. Chilingar, Sibel Pamukcu, J. K. Wittle, and Manal Abdel Aziz Al Badawi. "A Novel Electrokinetics Method of Oilfield Scale Control in-situ." In SPE Western Regional Meeting. Society of Petroleum Engineers, 2010. http://dx.doi.org/10.2118/133619-ms.
Full textYang, Kai, and Jie Wu. "In Situ Electrokinetic Preconcentrator for Conductive Biofluids." In ASME 2009 Second International Conference on Micro/Nanoscale Heat and Mass Transfer. ASMEDC, 2009. http://dx.doi.org/10.1115/mnhmt2009-18466.
Full textWrixon, Robert C., and George A. Cooper. "In-situ Casing Consolidation by Electrokinetic and Electrochemical Methods." In SPE Annual Technical Conference and Exhibition. Society of Petroleum Engineers, 1997. http://dx.doi.org/10.2118/38586-ms.
Full textOrtega-Tong, Pablo, James Jamieson, Riccardo Sprocati, Jing Sun, Massimo Rolle, Andy Fourie, and Henning Prommer. "Identification of Physical and Geochemical Controls on the Electrokinetic in situ Leaching of Gold." In Goldschmidt2020. Geochemical Society, 2020. http://dx.doi.org/10.46427/gold2020.1999.
Full textYang Wei, Sun Bingshuang, Zhou Hui, and Li shiliang. "Experimental study on electrokinetic remediation of in-situ Cd contaminated soil by applied voltage." In Environment (ICMREE). IEEE, 2011. http://dx.doi.org/10.1109/icmree.2011.5930701.
Full textCorral, Guillermo, and Nazmul Islam. "Bioparticle Manipulation by an Orthogonal Electrode Preconcentrator." In ASME 2015 International Mechanical Engineering Congress and Exposition. American Society of Mechanical Engineers, 2015. http://dx.doi.org/10.1115/imece2015-52724.
Full textRibeiro, A., J. Araújo, A. Mota, R. Campos, C. Vilarinho, and J. Carvalho. "Decontamination of Heavy Metals From Municipal Sewage Sludge (MSS) by Electrokinetic Remediation." In ASME 2019 International Mechanical Engineering Congress and Exposition. American Society of Mechanical Engineers, 2019. http://dx.doi.org/10.1115/imece2019-11221.
Full textReports on the topic "In-situ electrokinetics"
Pelletier, Austin, Amanda Hohner, Idil Deniz Akin, Indranil Chowdhury, Richard Watts, Xianming Shi, Brendan Dutmer, and James Mueller. Bench-scale Electrochemical Treatment of Co-contaminated Clayey Soil. Illinois Center for Transportation, June 2021. http://dx.doi.org/10.36501/0197-9191/21-018.
Full textDevelopment of an integrated, in-situ remediation technology: Task 2--4, electrokinetic modeling. Topical report, September 26--May 25, 1996. Office of Scientific and Technical Information (OSTI), May 1997. http://dx.doi.org/10.2172/473988.
Full text