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Journal articles on the topic 'Permeable reactive barrier p'

Author: Grafiati

Published: 6 September 2023

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1

Summers, Robert, and David Weaver. "Phosphorus Retention of a Permeable Reactive Barrier Surpassed by an Unvegetated Artificial Pond." Environment and Natural Resources Research 11, no. 1 (2021): 25. http://dx.doi.org/10.5539/enrr.v11n1p25.

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An artificial pond bisected by a phosphorus (P) retentive permeable reactive barrier (PRB) alongside Forrest Highway, Coolup, Western Australia was designed to remove P from farmland runoff. The pond bed was made of subsoil and road construction materials likely to have a relatively high P sorption capacity, and there was no vegetation in the bed of the pond. Flow through the pond was intercepted by the PRB, constructed from a mixture of sand, coarse crushed limestone, and bauxite residue (with 10% phospho-gypsum). The effectiveness of P removal and the impact of the PRB was measured by compar

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2

Hyodo, Fuminori, Kai-Hsiang Chuang, Artem G. Goloshevsky, et al. "Brain Redox Imaging Using Blood—Brain Barrier-Permeable Nitroxide MRI Contrast Agent." Journal of Cerebral Blood Flow & Metabolism 28, no. 6 (2008): 1165–74. http://dx.doi.org/10.1038/jcbfm.2008.5.

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Reactive oxygen species (ROS) and compromised antioxidant defense may contribute to brain disorders such as stroke, amyotrophic lateral sclerosis, etc. Nitroxides are redox-sensitive paramagnetic contrast agents and antioxidants. The ability of a blood—brain barrier (BBB)-permeable nitroxide, methoxycarbonyl-2,2,5,5-tetramethylpyrrolidine-1-oxyl (MC-P), as a magnetic resonance-imaging (MRI) contrast agent for brain tissue redox imaging was tested. MC-P relaxation in rodent brain was quantified by MRI using a fast Look-Locker T1-mapping sequence. In the cerebral cortex and thalamus, the MRI sig

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3

Soto-Rios, Paula Cecilia, Kazunori Nakano, Megumu Fujibayashi, Marco Leon-Romero, and Osamu Nishimura. "Lead removal efficiency using biosorbents as alternative materials for permeable reactive barriers." Water Science and Technology 70, no. 2 (2014): 307–14. http://dx.doi.org/10.2166/wst.2014.223.

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As alternative materials for heavy metal removal, this study investigated biosorbents to determine their suitability for permeable reactive barriers. The lead removal efficiencies of brown seaweed (Undaria pinnatifida) and reed (Phragmites australis) were determined under different conditions (batch and column system). The experimental results for these biomaterials fitted the Langmuir isotherm with high correlation values. It was verified that the influence of temperature on affinity was higher than that on adsorption capacity. While the lead removal efficiency of U. pinnatifida was higher th

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4

Bus, Agnieszka, Agnieszka Karczmarczyk, and Anna Baryła. "Permeable Reactive Barriers for Preventing Water Bodies from a Phosphorus-Polluted Agricultural Runoff-Column Experiment." Water 11, no. 3 (2019): 432. http://dx.doi.org/10.3390/w11030432.

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This paper aims to examine the potential of permeable reactive barriers (PRBs) as an in-situ removal approach for phosphate polluted agricultural runoff. Four different reactive materials (RMs) of: autoclaved aerated concrete (AAC), Polonite®, zeolite and limestone were tested. The study was conducted as a column experiment with a sandy loam soil type charging underlying RM layers with phosphorus (P) and a soil column without RM as a reference. The experiment was carried out over 90 days. During this time the P-PO4 load from the reference column equaled 6.393 mg and corresponds to 3.87 kg/ha.

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5

Choi, Jiyeon, Ardie Septian, and Won Sik Shin. "Influence of Salinity on the Removal of Ni and Zn by Phosphate-Intercalated Nano Montmorillonite (PINM)." Minerals 10, no. 11 (2020): 980. http://dx.doi.org/10.3390/min10110980.

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The salinity influence on the adsorptions of Ni and Zn onto phosphate-intercalated nano montmorillonite (PINM) were investigated. Single adsorption isotherm models fitted the single adsorption data well. The adsorption capacity of Ni was higher than that of Zn onto PINM at different salinities. The single adsorption parameters from Langmuir model (QmL and bL) were compared with the binary adsorption (QmL* and bL*). The QmL* of Zn was lower than that of Ni. The simultaneous presence of Ni and Zn decreased the adsorption capacities. The single and binary adsorptions onto PINM were affected by th

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6

Choi, Jiyeon, Ardie Septian, and Won Sik Shin. "The Influence of Salinity on the Removal of Ni and Zn by Sorption onto Iron Oxide- and Manganese Oxide-Coated Sand." Sustainability 12, no. 14 (2020): 5815. http://dx.doi.org/10.3390/su12145815.

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The influence of salinity on the single and binary sorption of Ni and Zn onto iron oxide- and manganese oxide-coated sand (IOCS and MOCS) was investigated at pH = 5. The single sorption experimental data were fitted to Freundlich, Langmuir, Dubinin–Radushkevich, and Sips models, and a nonlinear sorption isotherm was observed (NF = 0.309–0.567). The higher Brunauer–Emmett–Teller (BET) surface area (ABET) and cation exchange capacity (CEC) of MOCS contributed to the higher maximum sorption capacities (qmL) of Ni and Zn than that of IOCS. The Ni sorption capacities in the single sorption were hig

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7

Murphy, Kelsey, Killian Llewellyn, Samuel Wakser, et al. "Mini-GAGR, an intranasally applied polysaccharide, activates the neuronal Nrf2-mediated antioxidant defense system." Journal of Biological Chemistry 293, no. 47 (2018): 18242–69. http://dx.doi.org/10.1074/jbc.ra117.001245.

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Oxidative stress triggers and exacerbates neurodegeneration in Alzheimer's disease (AD). Various antioxidants reduce oxidative stress, but these agents have little efficacy due to poor blood–brain barrier (BBB) permeability. Additionally, single-modal antioxidants are easily overwhelmed by global oxidative stress. Activating nuclear factor erythroid 2 (NF-E2)-related factor 2 (Nrf2) and its downstream antioxidant system are considered very effective for reducing global oxidative stress. Thus far, only a few BBB-permeable agents activate the Nrf2-dependent antioxidant system. Here, we discovere

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8

Schwarz, Alex O., and Bruce E. Rittmann. "The diffusion-active permeable reactive barrier." Journal of Contaminant Hydrology 112, no. 1-4 (2010): 155–62. http://dx.doi.org/10.1016/j.jconhyd.2009.12.004.

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9

Thiruvenkatachari, R., S. Vigneswaran, and R. Naidu. "Permeable reactive barrier for groundwater remediation." Journal of Industrial and Engineering Chemistry 14, no. 2 (2008): 145–56. http://dx.doi.org/10.1016/j.jiec.2007.10.001.

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10

Banasiak, Laura Joan, Buddhima Indraratna, Glenys Lugg, Udeshini Pathirage, Geoff McIntosh, and Neil Rendell. "Permeable reactive barrier rejuvenation by alkaline wastewater." Environmental Geotechnics 2, no. 1 (2015): 45–55. http://dx.doi.org/10.1680/envgeo.13.00122.

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11

Molfetta, Antonio Di, and Rajandrea Sethi. "Clamshell excavation of a permeable reactive barrier." Environmental Geology 50, no. 3 (2006): 361–69. http://dx.doi.org/10.1007/s00254-006-0215-3.

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12

Tigue, April Anne, Roy Alvin Malenab, and Michael Angelo Promentilla. "A systematic mapping study on the development of permeable reactive barrier for acid mine drainage treatment." MATEC Web of Conferences 268 (2019): 06019. http://dx.doi.org/10.1051/matecconf/201926806019.

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Acid mine drainage is a result of exposure of sulfide ore and minerals to water and oxygen. This environmental pollutant has been considered the second biggest environmental problem after global warming. On the other hand, permeable reactive barrier is an emerging remediation technology which can be used to treat acid mine drainage. However, the effectiveness of this proposed remediation technology greatly depends on the reactive media. Also, treatment of acid mine drainage using permeable reactive barrier is still in the infancy stage, and long-term performance is still unknown. Hence, this s

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13

Bus, Agnieszka, Agnieszka Karczmarczyka, and Anna Baryła. "Phosphorus reactive materials for permeable reactive barrier filling – lifespan estimations." DESALINATION AND WATER TREATMENT 244 (2021): 194–200. http://dx.doi.org/10.5004/dwt.2021.27905.

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14

Bus, Agnieszka, Agnieszka Karczmarczyka, and Anna Baryła. "Phosphorus reactive materials for permeable reactive barrier filling – lifespan estimations." DESALINATION AND WATER TREATMENT 245 (2022): 9–15. http://dx.doi.org/10.5004/dwt.2022.27905.

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15

Oliveira, M., Ana Vera Machado, and Regina Nogueira. "Development of Permeable Reactive Barrier for Phosphorus Removal." Materials Science Forum 636-637 (January 2010): 1365–70. http://dx.doi.org/10.4028/www.scientific.net/msf.636-637.1365.

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Permeable reactive barriers were developed for phosphorus removal. The barrier consists in an organic-inorganic hybrid material, which allows water and others species to flow through it, while selectively removes the contaminants. Polyethylene oxide (POE) and aluminium oxide (Al2O3) were used as the organic and the inorganic parts, respectively. The hybrid material was obtained by sol-gel reaction, using aluminium isopropoxide as inorganic percursor in order to attain Al2O3. The hybrid material produced was characterized by FT-IR spectroscopy and thermogravimetry. The previous tests for phosph

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16

He, Qianfeng, Shihui Si, Jun Yang, and Xiaoyu Tu. "Application of permeable reactive barrier in groundwater remediation." E3S Web of Conferences 136 (2019): 06021. http://dx.doi.org/10.1051/e3sconf/201913606021.

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As a new in-situ remediation of groundwater, compared with the traditional “pump and treat” technology, the permeable reactive barrier (PRB) has the advantages of low cost, no external power, the small disturbance to groundwater, small secondary pollution and long-term operation, this paper introduces the basic concept of PRB, technical principle, structure type, the principle of active materials selection and mechanisms of remediation, design and installation factors, it provides ideas for further research and application of PRB technology in groundwater remediation projects in China.

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17

Lee, Jejung, Andrew J. Graettinger, John Moylan, and Howard W. Reeves. "Directed site exploration for permeable reactive barrier design." Journal of Hazardous Materials 162, no. 1 (2009): 222–29. http://dx.doi.org/10.1016/j.jhazmat.2008.05.026.

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18

Morgan, Lynn A., Don Ficklen, and Mary Knowles. "Site characterization to support permeable reactive barrier design." Remediation Journal 15, no. 4 (2005): 63–71. http://dx.doi.org/10.1002/rem.20060.

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19

Lachowicz, Jean E., Michel Demeule, Anthony Regina, et al. "Using ANG4043, a brain-penetrant anti-HER2 mab, to increase survival in a murine intracranial breast tumor model." Journal of Clinical Oncology 31, no. 15_suppl (2013): e13013-e13013. http://dx.doi.org/10.1200/jco.2013.31.15_suppl.e13013.

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e13013 Background: Treatments for metastatic brain tumors originating from HER2-positive breast disease are limited due to the inability of most anti-tumor agents to enter the brain. While the selectively permeable blood-brain barrier (BBB) restricts access of therapeutics such as mAbs to the brain, transcytosis of hormones, nutrients, and other homeostatic modulators is mediated by endogenous receptors such as LRP1, low density lipoprotein receptor-related protein 1. We have created a family of peptides (Angiopeps) that are recognized by LRP1 and enter the brain via transcytosis. Using these

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20

Ludwig, Ralph D., Rick G. McGregor, David W. Blowes, Shawn G. Benner, and Keith Mountjoy. "A Permeable Reactive Barrier for Treatment of Heavy Metals." Ground Water 40, no. 1 (2002): 59–66. http://dx.doi.org/10.1111/j.1745-6584.2002.tb02491.x.

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21

Richards, Peter. "Seven‐year performance evaluation of a permeable reactive barrier." Remediation Journal 18, no. 3 (2008): 63–78. http://dx.doi.org/10.1002/rem.20172.

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22

Muegge, John P., and Paul W. Hadley. "An evaluation of permeable reactive barrier projects in California." Remediation Journal 20, no. 1 (2009): 41–57. http://dx.doi.org/10.1002/rem.20228.

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23

Vesela, Lenka, Jan Nemecek, Martina Siglova, and Martin Kubal. "The biofiltration permeable reactive barrier: Practical experience from Synthesia." International Biodeterioration & Biodegradation 58, no. 3-4 (2006): 224–30. http://dx.doi.org/10.1016/j.ibiod.2006.06.013.

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24

Xue, Fengjiao, Yujie Yan, Ming Xia, et al. "Electro-kinetic remediation of chromium-contaminated soil by a three-dimensional electrode coupled with a permeable reactive barrier." RSC Advances 7, no. 86 (2017): 54797–805. http://dx.doi.org/10.1039/c7ra10913j.

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25

Slater, Lee, and Andrew Binley. "Evaluation of permeable reactive barrier (PRB) integrity using electrical imaging methods." GEOPHYSICS 68, no. 3 (2003): 911–21. http://dx.doi.org/10.1190/1.1581043.

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The permeable reactive barrier (PRB) is a promising in‐situ technology for treatment of hydrocarbon‐contaminated groundwater. A PRB is typically composed of granular iron which degrades chlorinated organics into potentially nontoxic dehalogenated organic compounds and inorganic chloride. Geophysical methods may assist assessment of in‐situ barrier integrity and evaluation of long‐term barrier performance. The highly conductive granular iron makes the PRB an excellent target for conductivity imaging methods. In addition, electrochemical storage of charge at the iron–solution interface generates

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26

Indraratna, Buddhima, Punyama Udeshini Pathirage, and Laura Joan Banasiak. "Remediation of acidic groundwater by way of permeable reactive barrier." Environmental Geotechnics 4, no. 4 (2017): 284–98. http://dx.doi.org/10.1680/envgeo.14.00014.

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27

Golab, Alexandra N., Buddhima Indraratna, Mark A. Peterson, and Stephen Hay. "Design of a Permeable Reactive Barrier to Remediate Acidic Groundwater." ASEG Extended Abstracts 2006, no. 1 (2006): 1–3. http://dx.doi.org/10.1071/aseg2006ab051.

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28

Hosseini, S. Mossa, B. Ataie-Ashtiani, and M. Kholghi. "Bench-Scaled Nano-Fe0 Permeable Reactive Barrier for Nitrate Removal." Ground Water Monitoring & Remediation 31, no. 4 (2011): 82–94. http://dx.doi.org/10.1111/j.1745-6592.2011.01352.x.

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29

Kennedy, Lonnie G., and Jess W. Everett. "Field application of biogeochemical reductive dechlorination by permeable reactive barrier." International Journal of Environment and Waste Management 14, no. 4 (2014): 323. http://dx.doi.org/10.1504/ijewm.2014.066590.

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30

Richards, Peter. "Construction of a permeable reactive barrier in a residential neighborhood." Remediation Journal 12, no. 4 (2002): 65–79. http://dx.doi.org/10.1002/rem.10046.

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31

Ribeiro, André, André Mota, Margarida Soares, Carlos Castro, Jorge Araújo, and Joana Carvalho. "Lead (II) Removal from Contaminated Soils by Electrokinetic Remediation Coupled with Modified Eggshell Waste." Key Engineering Materials 777 (August 2018): 256–61. http://dx.doi.org/10.4028/www.scientific.net/kem.777.256.

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Electrokinetic remediation deserves particular attention in soil treatment due to its peculiar advantages, including the capability of treating fine and low permeability materials, and achieving consolidation, dewatering and removal of salts and inorganic contaminants like heavy metals in a single stage. In this study, the remediation of artificially lead (II) contaminated soil by electrokinetic process, coupled with Eggshell Inorganic Fraction Powder (EGGIF) permeable reactive barrier (PRB), was investigated. An electric field of 2 V cm-1was applied and was used an EGGIF/soil ratio of 30 g kg

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32

Faisal, Ayad Abdulhamza, and Zaman Ageel Hmood. "Modeling and Simulation of Cadmium Removal from the Groundwater by Permeable Reactive Barrier Technology." Journal of Engineering 20, no. 04 (2023): 134–59. http://dx.doi.org/10.31026/j.eng.2014.04.09.

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The removal of cadmium ions from simulated groundwater by zeolite permeable reactive barrier was investigated. Batch tests have been performed to characterize the equilibrium sorption properties of the zeolite in cadmium-containing aqueous solutions. Many operating parameters such as contact time, initial pH of solution, initial concentration, resin dosage and agitation speed were investigated. The best values of these parameters that will achieved removal efficiency of cadmium (=99.5%) were 60 min, 6.5, 50 mg/L, 0.25 g/100 ml and 270 rpm respectively. A 1D explicit finite difference model has

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33

Peng, Shengjie, Xiaodong Wang, and Xiaohui Zhang. "Research progress of in-situ remediation of polluted soil and groundwater by electrokinetic and permeable reaction barrier." E3S Web of Conferences 143 (2020): 02043. http://dx.doi.org/10.1051/e3sconf/202014302043.

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The combination of electrokinetic remediation and permeable reactive barrier (EK-PRB combined remediation technology) is a new green technology for in-situ removal of soil and groundwater pollutants. This technology combines the advantages of electrokinetic remediation and permeable reactive barrier technology, and can deal with different types of organic and inorganic pollutants. It has the characteristics of convenient installation, simple operation, no secondary pollution, etc., and has broad development and application prospect. This paper introduces the technical principle of EK-PRB, summ

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34

Meng, Ruihong, Tan Chen, Yaxin Zhang, et al. "Development, modification, and application of low-cost and available biochar derived from corn straw for the removal of vanadium(v) from aqueous solution and real contaminated groundwater." RSC Advances 8, no. 38 (2018): 21480–94. http://dx.doi.org/10.1039/c8ra02172d.

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35

Faisal, Ayad Abdulhamza, Talib Rasheed Abbas, and Salim Hrez Jassam. "Iron Permeable Reactive Barrier for Removal of Lead from Contaminated Groundwater." Journal of Engineering 20, no. 10 (2023): 29–46. http://dx.doi.org/10.31026/j.eng.2014.10.03.

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The possibility of using zero-valent iron as permeable reactive barrier in removing lead from a contaminated groundwater was investigated. In the batch tests, the effects of many parameters such as contact time between adsorbate and adsorbent (0-240 min), initial pH of the solution (4-8), sorbent dosage (1-12 g/100 mL), initial metal concentration (50-250 mg/L), and agitation speed (0-250 rpm) were studied. The results proved that the best values of these parameters achieve the maximum removal efficiency of Pb+2 (=97%) were 2 hr, 5, 5 g/100 mL, 50 mg/L and 200 rpm respectively. The sorption da

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36

Budihardjo, M. A., R. P. Safitri, B. S. Ramadan, et al. "A bibliometric analysis of permeable reactive barrier enhanced electrokinetic treatment for sustainable polluted soil remediation." IOP Conference Series: Earth and Environmental Science 894, no. 1 (2021): 012034. http://dx.doi.org/10.1088/1755-1315/894/1/012034.

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Abstract Research on soil remediation continues to develop, one of which is electrokinetic remediation combined with a permeable reactive barrier as a medium to prevent the migration of metals removed from the anode and cathode spaces. Thus, it is hoped that there is no need for reprocessing the residue resulting from electrokinetic remediation. This study aims to conduct a bibliographical analysis related to electrokinetic remediation coupled by permeable reactive barriers for heavy metal contaminated soil and to examine the effect of using various types of reactive barrier materials and thei

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37

Schwarz, Alex, and Norma Pérez. "Long-term operation of a permeable reactive barrier with diffusive exchange." Journal of Environmental Management 284 (April 2021): 112086. http://dx.doi.org/10.1016/j.jenvman.2021.112086.

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38

Kim, Young-Hun, and Myung-Chul Kim. "Development of Activity Enhanced Zero Valent Metals for Permeable Reactive Barrier." Journal of Environmental Science International 12, no. 2 (2003): 201–5. http://dx.doi.org/10.5322/jes.2003.12.2.201.

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39

Moraci, Nicola, Stefania Bilardi, and Paolo S. Calabrò. "Fe0/pumice mixtures: from laboratory tests to permeable reactive barrier design." Environmental Geotechnics 4, no. 4 (2017): 245–56. http://dx.doi.org/10.1680/jenge.15.00002.

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40

Chiemchaisri, Chart, Wilai Chiemchaisri, and Chayanid Witthayapirom. "Remediation of MSW landfill leachate by permeable reactive barrier with vegetation." Water Science and Technology 71, no. 9 (2015): 1389–97. http://dx.doi.org/10.2166/wst.2015.111.

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This research was conducted to investigate in situ treatment of leachate by pilot-scale permeable reactive barrier (PRB) with vegetation. Two different types of PRB media, with and without the presence of ferric chloride sludge, for the removal of pollutants were examined. The composite media of PRB comprised a clay and sand mixture of 40:60%w/w (system 1) and a clay, ferric chloride sludge and sand mixture of 30:10:60%w/w (system 2). The system was operated at a hydraulic loading rate of 0.028 m3/m2.d and hydraulic retention time of 10 days. The results showed that the performance of system 2

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41

Bartlett, T. R., and S. J. Morrison. "Tracer Method to Determine Residence Time in a Permeable Reactive Barrier." Ground Water 47, no. 4 (2009): 598–604. http://dx.doi.org/10.1111/j.1745-6584.2009.00544.x.

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42

Johnson, R. L., R. B. Thoms, R. O’Brien Johnson, J. T. Nurmi, and P. G. Tratnyek. "Mineral Precipitation Upgradient from a Zero-Valent Iron Permeable Reactive Barrier." Ground Water Monitoring & Remediation 28, no. 3 (2008): 56–64. http://dx.doi.org/10.1111/j.1745-6592.2008.00203.x.

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43

Van Nooten, Thomas, Dirk Springael, and Leen Bastiaens. "Microbial Community Characterization in a Pilot-Scale Permeable Reactive Iron Barrier." Environmental Engineering Science 27, no. 3 (2010): 287–92. http://dx.doi.org/10.1089/ees.2009.0271.

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44

Courcelles, Benoît, Arezou Modaressi-Farahmand-Razavi, Daniel Gouvenot, and Annette Esnault-Filet. "Influence of Precipitates on Hydraulic Performance of Permeable Reactive Barrier Filters." International Journal of Geomechanics 11, no. 2 (2011): 142–51. http://dx.doi.org/10.1061/(asce)gm.1943-5622.0000098.

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45

Serrenho, A., O. Fenton, M. Rodgers, and M. G. Healy. "Laboratory study of a denitrification system using a permeable reactive barrier." Advances in Animal Biosciences 1, no. 1 (2010): 88. http://dx.doi.org/10.1017/s2040470010002311.

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46

Morrison, Stan J., Paul S. Mushovic, and Preston L. Niesen. "Early Breakthrough of Molybdenum and Uranium in a Permeable Reactive Barrier." Environmental Science & Technology 40, no. 6 (2006): 2018–24. http://dx.doi.org/10.1021/es052128s.

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47

Yang, Ji, Yuling Guo, Decai Xu, Limei Cao, and Jinping Jia. "A controllable Fe0–C permeable reactive barrier for 1,4-dichlorobenzene dechlorination." Chemical Engineering Journal 203 (September 2012): 166–73. http://dx.doi.org/10.1016/j.cej.2012.07.031.

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48

Ono, Yusaku, Mikio Kawasaki, Yoichi Watanabe, Masato Yamada, Kazuto Endo, and Yoshiro Ono. "Horizontal Permeable Reactive Barrier for Improving the Water Quality within Landfills." Journal of the Japan Society of Waste Management Experts 19, no. 3 (2008): 197–211. http://dx.doi.org/10.3985/jswme.19.197.

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49

Mumford, K. A., J. L. Rayner, I. Snape, and G. W. Stevens. "Hydraulic performance of a permeable reactive barrier at Casey Station, Antarctica." Chemosphere 117 (December 2014): 223–31. http://dx.doi.org/10.1016/j.chemosphere.2014.06.091.

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50

Folch, Albert, Marcel Vilaplana, Leila Amado, Teresa Vicent, and Glòria Caminal. "Fungal permeable reactive barrier to remediate groundwater in an artificial aquifer." Journal of Hazardous Materials 262 (November 2013): 554–60. http://dx.doi.org/10.1016/j.jhazmat.2013.09.004.

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