Relevant bibliographies by topics / Trichloroethylene

Academic literature on the topic 'Trichloroethylene'

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Published: 4 June 2021
Last updated: 29 July 2024

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Journal articles on the topic "Trichloroethylene"

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&NA;. "Trichloroethylene." Reactions Weekly &NA;, no. 850 (May 2001): 11. http://dx.doi.org/10.2165/00128415-200108500-00029.

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Stetson, J. B. "Trichloroethylene." Anaesthesia 43, no. 11 (November 1988): 991. http://dx.doi.org/10.1111/j.1365-2044.1988.tb05676.x.

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Cooper, E. A. "Trichloroethylene." Anaesthesia 43, no. 5 (May 1988): 420. http://dx.doi.org/10.1111/j.1365-2044.1988.tb09038.x.

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Vittal Prasad, T. E., S. B. Agrawal, A. B. Bajaj, and D. H. L. Prasad. "Density and Viscosity of Methanol + Trichloroethylene,n-Propanol + Trichloroethylene andn-Butanol + Trichloroethylene Mixtures." Physics and Chemistry of Liquids 38, no. 4 (July 2000): 433–38. http://dx.doi.org/10.1080/00319100008030290.

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Forkert, P. G., and L. Forkert. "Trichloroethylene induces pulmonary fibrosis in mice." Canadian Journal of Physiology and Pharmacology 72, no. 3 (March 1, 1994): 205–10. http://dx.doi.org/10.1139/y94-032.

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Trichloroethylene elicits acute pulmonary cytotoxicity in mice, which involves Clara cells of bronchioles. In this study, we have examined the effects of an acute dose of trichloroethylene in lungs of mice over 3 months. Pulmonary fibrosis was first detected at 15 days and was progressive with time elapsed after trichloroethylene exposure. Diffuse interstitial fibrosis was observed in the alveolar zone, resulting in thickening of alveolar septa and distortion of lung structure. The fibrosis was most pronounced at 90 days after treatment, resulting in deposition of connective tissue in the alveolar septa. Levels of total lung hydroxyproline were not significantly different in control and treated mice at 30 and 60 days after trichloroethylene treatment, but were significantly increased at 90 days. Proline content remained unchanged during the course of this study. The increase in collagen deposition at 90 days coincided with a signficant increase in lung elastic recoil. Our results show that a single acute dose of trichloroethylene causes structural and functional abnormalities that are progressive for at least 3 months.Key words: trichloroethylene, lung, interstitial fibrosis.
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&NA;. "Trichloroethylene overdose?" Reactions Weekly &NA;, no. 1064 (August 2005): 14. http://dx.doi.org/10.2165/00128415-200510640-00033.

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Balakrishnan, C., Mark W. Leonard, and Dean Marson. "Trichloroethylene “Burn”." Journal of Burn Care & Rehabilitation 14, no. 4 (July 1993): 461–62. http://dx.doi.org/10.1097/00004630-199307000-00012.

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Vanderberg, Laura A., Brian L. Burback, and Jerome J. Perry. "Biodegradation of trichloroethylene by Mycobacterium vaccae." Canadian Journal of Microbiology 41, no. 3 (March 1, 1995): 298–301. http://dx.doi.org/10.1139/m95-041.

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Nonproliferating cells of Mycobacterium vaccae that were grown on propane could mineralize limited amounts of trichloroethylene. Intermediates in the biodegradation of trichloroethylene were 2,2,2-trichloroethanol and 2,2,2-trichloroacetaldehyde. Trichloroethanol was completely degraded when added to a nonproliferating cell suspension of Mycobacterium vaccae. Addition of toluene to the reaction mixtures effected a 50% increase in the mineralization of [14C]trichloroethylene.Key words: trichloroethylene, cometabolism, Mycobacterium vaccae.
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Vyskocil, A., T. Leroux, G. Truchon, F. Lemay, F. Gagnon, M. Gendron, and C. Viau. "Ototoxicity of trichloroethylene in concentrations relevant for the working environment." Human & Experimental Toxicology 27, no. 3 (March 2008): 195–200. http://dx.doi.org/10.1177/0960327108090267.

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Organic solvents can cause hearing loss themselves or promote noise-induced hearing loss. The objective of this study was to review the literature on the effects of low-level exposure to trichloroethylene on the auditory system and consider its relevance for the occupational settings. Both human and animal investigations were evaluated only for realistic exposure concentrations based on the Quebec permissible exposure limits: 50 ppm 8-h time-weighed average exposure value (TWAEV) and 200 ppm short-term exposure value (STEV). In humans, the upper limit for considering ototoxicity data relevant to the occupational exposure situation was set at the STEV. Animal data were evaluated only for exposure concentrations up to 100 times the TWAEV. There is no convincing evidence of trichloroethylene-induced hearing losses in workers. In rats, trichloroethylene affects the auditory function mainly in the cochlear mid- to high-frequency range with a lowest observed adverse effect level (LOAEL) of 2000 ppm. No studies on ototoxic interaction after combined exposure to noise and trichloroethylene were identified in humans. In rats, supra-additive interaction was reported. Further studies with sufficient data on the trichloroethylene exposure of workers are necessary to make a definitive conclusion. In the interim, we recommend considering trichloroethylene as an ototoxic agent.
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Rhee, E., and R. E. Speece. "Maximal Biodegradation Rates of Chloroform and Trichloroethylene in Anaerobic Treatment." Water Science and Technology 25, no. 3 (February 1, 1992): 121–30. http://dx.doi.org/10.2166/wst.1992.0085.

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Computer controlled reactors were used to determine the maximal rate of anaerobic biodegradation of chloroform and trichloroethylene using three important anaerobic intermediates (propionate, hydrogen, and acetate) as primary substrates. Maximal biodegradation rate was defined as that loading rate of chloroform and trichloroethylene which can be achieved while reducing process efficiency of the primary substrate to 50 %. The systems were controlled by a computer in response to the pH of the reactor in order to establish the unlimited equilibrium utilization levels of the three primary substrates and the chlorinated aliphatic compounds. From 89 to 99 % of chloroform and trichloroethylene was biodegraded at maximal loading rate of 15-109 mg/l of reactor-day in the primary substrate enrichment cultures. Biodegradation potentials, the affected class of microorganisms, and the fate and metabolic intermediates of chloroform and trichloroethylene also were examined.
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Dissertations / Theses on the topic "Trichloroethylene"

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Yaqoob, Noreen. "Studies on trichloroethylene-induced formic aciduria." Thesis, Liverpool John Moores University, 2010. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.526913.

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Randall, Debra Jean 1955. "TUMOR-PROMOTING EFFECTS OF TRICHLOROETHYLENE (NEONATAL, MOUSE)." Thesis, The University of Arizona, 1986. http://hdl.handle.net/10150/291251.

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Wei, Zongsu. "Trichloroethylene (TCE) Adsorption Using Sustainable Organic Mulch." University of Toledo / OhioLINK, 2010. http://rave.ohiolink.edu/etdc/view?acc_num=toledo1279301053.

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Mishra, Dhananjay. "Electrochemical Deactivation of Nitrate, Arsenate, and Trichloroethylene." Diss., The University of Arizona, 2006. http://hdl.handle.net/10150/194084.

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This research investigated the mechanism, kinetics and feasibility of nitrate, arsenate, and trichloroethylene inactivation on zerovalent iron (ZVI), mixed-valent iron oxides, and boron doped diamond film electrode surfaces, respectively. Nitrate ( ) is a common co-contaminant at sites remediated using permeable reactive barriers (PRBs). Therefore, understanding nitrate reactions with ZVI is important for understanding the performance of PRBs. This study investigated the reaction mechanisms of with ZVI under conditions relevant to groundwater treatment. Tafel analysis and electrochemical impedance spectroscopy were used to probe the surface reactions. Batch experiments were used to study the reaction rate of with freely corroding and cathodically protected iron wires. The removal kinetics for the air formed oxide (AFO) were 2.5 times slower than that of water formed oxide (WFO).This research also investigated the use of slowly corroding magnetite (Fe3O4) and wustite (FeO) as reactive adsorbent media for removing As(V) from potable water. Observed corrosion rates for mixed valent iron oxides were found to be 15 times slower than that of zerovalent iron under similar conditions. Electrochemical and batch and column experiments were performed to study the corrosion behavior and gain a deeper understanding on the effects of water chemistry and operating parameters, such as, empty bed contact times, influent arsenic concentrations, dissolved oxygen levels and solution pH values and other competing ions. Reaction products were analyzed by X-Ray diffraction and XPS to determine the fate of the arsenic.This research also investigated use of boron doped diamond film electrodes for reductive dechlorination of trichloroethylene (TCE). TCE reduction resulted in nearly stoichiometric production of acetate. Rates of TCE reduction were found to be independent of the electrode potential at potentials below -1 V with respect to the standard hydrogen electrode (SHE). However, at smaller overpotentials, rates of TCE reduction were dependent on the electrode potential. Short lived species analysis and density functional simulations indicate that TCE reduction may occur by formation of a surface complex between TCE and carbonyl groups present on the surface.
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Makwana, Om. "THE EFFECTS OF TRICHLOROETHYLENE ON HEART DEVELOPMENT." Diss., The University of Arizona, 2010. http://hdl.handle.net/10150/204310.

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Trichloroethylene (TCE; TRI; C2HCl3) is an organic solvent used as an industrial degreasing agent. Due to its widespread use and volatile nature, TCE is a common environmental contaminant. Trichloroethylene exposure has been implicated in the etiology of heart defects in human populations and animal models. Recent data suggest misregulation of Ca2+ homeostasis in a cardiomyocyte cell line after TCE exposure (Caldwell, Thorne et al. 2008). We hypothesized that misregulation of Ca2+ homeostasis alters myocyte function and leads to changes in embryonic blood flow. In turn, changes in cardiac flow are known to cause cardiac malformations. To investigate this hypothesis we dosed developing chick embryos in ovo with environmentally relevant doses of TCE (8 ppb and 800 ppb). We then isolated RNA from embryos at crucial time points in development for real-time PCR analysis of markers for altered blood flow. Based on this analysis, we observed effects on ET-1 (Endothelin-1), NOS-3 (Nitric Oxide Synthase-3) and Krüppel-Like Factor 2 (KLF2) expression relative to TCE exposure. Additionally, we assessed cardiomyocyte function by isolating chick E18 cardiomyocytes from embryos exposed to TCE in ovo. Cells were measured for rate of contraction after pulsing with extracellular Ca2+ and electrical stimulation at a frequency of 1.0 Hz. These functional data showed an effect on Ca2+ handling in cardiomyocytes exposed to TCE. To investigate an apparent non-monotypic effect in the heart where 8 ppb produced a stronger effect than 800 ppb, we isolated RNA from the developing heart and AV Canal to investigate the expression of several candidate Cytochrome P450s (CYPs) related to TCE metabolism. We observed a significant induction of multiple CYP2 family members in the developing heart after low dose TCE exposure. Together, these data suggest cardio-specificity of TCE as a teratogen and may reflect a requirement for normal calcium regulation of contractile function during organ development.
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Lee, Seung-Bong. "Biodegradation of chlorinated ethene by pseudonocardia chlorethenivorans SL-1 /." Thesis, Connect to this title online; UW restricted, 2002. http://hdl.handle.net/1773/10109.

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Shanbhogue, Sai Sharanya. "Alginate Encapsulated Nanoparticle-Microorganism System for Trichloroethylene Remediation." Thesis, North Dakota State University, 2012. https://hdl.handle.net/10365/26675.

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Nanoscale zero-valent iron (NZVI) particles were encapsulated in calcium alginate capsules for application in environmental remediation. TCE degradation rates for encapsulated and bare NZVI were similar indicating no adverse effects of encapsulation on degradation kinetics. Microorganisms were separately encapsulated and used along with encapsulated NZVI and co-encapsulated in calcium alginate capsules. Batch experiments were performed to test the efficacy of the combined iron-Pseudomonas sp. (PpF1) system. The combined system removed 100% TCE over the first three hours of the experiment followed by 70% TCE removal post TCE re-dosing. Complete reduction of TCE was achieved by NZVI between 0-3 h and the second phase of treatment (3-36 h) was mostly achieved by microorganisms. Experiments conducted with co-encapsulated NZVI-D.BAV1 achieved 100% TCE removal. During the first three hours of the experiment 100% TCE removal was achieved by NZVI, and 100% removal was achieved post re-dosing where D.BAV1 accomplished the treatment.
Department of Civil Engineering, North Dakota State University
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Culpepper, Johnathan D. "Reduction of tetrachloroethylene and trichloroethylene by magnetite revisted." Thesis, University of Iowa, 2017. https://ir.uiowa.edu/etd/5741.

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For this study, we revisited whether the common iron Fe mineral, magnetite Fe3O4 (s), can reduce tetrachloroethylene (PCE) and trichloroethylene (TCE) as discrepancies exist in the literature regarding rates and extent of reduction. We measured PCE and TCE reduction in batch reactors as a function of magnetite stoichiometry (x = Fe2+/Fe3+ ratio), solids loading, pH, and Fe(II) concentration. Our results show that magnetite reacts only slowly with TCE (t1/2 = 7.6 years) and is not reactive with PCE over 150 days. The addition of aqueous Fe(II) to magnetite suspensions, however, results in slow, but measurable PCE and TCE reduction under some conditions. The solubility of ferrous hydroxide, Fe(OH)2(s), appears to play an important role in whether magnetite reduces PCE and TCE. In addition, we found that Fe(OH)2(s) reduces PCE and TCE at high Fe(II) concentrations as well. At certain conditions degradation of the PCE and TCE is enhanced by an unexplored synergistic response from magnetite and ferrous hydroxide iron phases. Our work suggests that measuring dissolved Fe(II) concentration and pH may be used as indicators to predict whether PCE and TCE will be abiotically degraded by groundwater aquifer solids containing magnetite.
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Wang, Lei. "Tetrachloroethene (PCE) and trichloroethene (TCE) biogradation with bioreactors /." free to MU campus, to others for purchase, 2001. http://wwwlib.umi.com/cr/mo/fullcit?p3036865.

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Costanza, Jed. "Degradation of tetrachloroethylene and trichloroethylene under thermal remediation conditions." Diss., Available online, Georgia Institute of Technology, 2005, 2005. http://etd.gatech.edu/theses/available/etd-08262005-021152/.

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Thesis (Ph. D.)--Civil & Environmental Engineering, Georgia Institute of Technology, 2006.
Pennell, Kurt, Committee Chair ; Lawrence Bottomley, Committee Member ; James Mulholland, Committee Member ; Carolyn Ruppel, Committee Member ; D. Webster, Committee Member. Includes bibliographical references.
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Books on the topic "Trichloroethylene"

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Programme, United Nations Environment, International Labour Organisation, and World Health Organization, eds. Trichloroethylene. Geneva: World Health Organization, 1985.

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United States. Agency for Toxic Substances and Disease Registry. Division of Toxicology. Trichloroethylene. Atlanta, GA: Dept. of Health and Human Services, Public Health Service, Agency for Toxic Substances and Disease Registry, Division of Toxicology, 1997.

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United States. Environmental Protection Agency, ed. Toxicological profile for trichloroethylene. Atlanta: Department of Health & Human Services, Public Health Service, Centers for Disease Control, 1989.

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United States. Public Health Service., United States. Agency for Toxic Substances and Disease Registry., and Clement International Corporation, eds. Toxicological profile for trichloroethylene. [Washington, D.C.]: U.S. Department of Health & Human Services, 1993.

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Gilbert, Kathleen M., and Sarah J. Blossom, eds. Trichloroethylene: Toxicity and Health Risks. London: Springer London, 2014. http://dx.doi.org/10.1007/978-1-4471-6311-4.

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United States. Environmental Protection Agency. Emission Standards and Engineering Division, ed. Survey of trichloroethylene emission sources. Research Triangle Park, N.C: U.S. Environmental Protection Agency, Office of Air and Radiation, Office of Air Quality Planning and Standards, 1985.

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Directorate, Canada Inland Waters. Canadian water quality guidelines for trichloroethylene. Ottawa, Ont: Inland Waters Directorate, 1991.

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United States. Agency for Toxic Substances and Disease Registry. Division of Toxicology. Tricloroetileno. Atlanta, GA: Departamento de Salud y Servicios Humanos de los EE.UU., Servicio de Salud Pública Agencia para Sustancias Tóxicas y el Registro de Enfermedades, División de la Toxicología y Medicina Ambiental, 1997.

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P, Beliles Robert, and United States. Environmental Protection Agency, eds. Consideration of the target organ toxicity of trichloroethylene in terms of metabolite toxicity and pharmacokinetics. [Washington, D.C: U.S. Environmental Protection Agency, 1992.

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V, Rood Robert, Atkinson Roger, and California. Air Resources Board. Stationary Source Division., eds. Proposed identification of trichloroethylene as a toxic air contaminant: Technical support document : report to the Air Resources Board on trichloroethylene (TCE). [Sacramento, CA]: State of California, Air Resources Board, Stationary Source Division, 1990.

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Book chapters on the topic "Trichloroethylene"

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Dodge, David G., and Julie E. Goodman. "Trichloroethylene." In Hamilton & Hardy's Industrial Toxicology, 733–40. Hoboken, New Jersey: John Wiley & Sons, Inc., 2015. http://dx.doi.org/10.1002/9781118834015.ch72.

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Ware, George W. "Trichloroethylene." In Reviews of Environmental Contamination and Toxicology, 203–12. New York, NY: Springer New York, 1988. http://dx.doi.org/10.1007/978-1-4612-3922-2_18.

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Gooch, Jan W. "Trichloroethylene." In Encyclopedic Dictionary of Polymers, 763. New York, NY: Springer New York, 2011. http://dx.doi.org/10.1007/978-1-4419-6247-8_12091.

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Patnaik, Pradyot. "Trichloroethylene." In Handbook of Environmental Analysis, 519–20. Third edition. | Boca Raton : Taylor & Francis, CRC Press, 2017.: CRC Press, 2017. http://dx.doi.org/10.1201/9781315151946-136.

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Howard, Philip H., Gloria W. Sage, William F. Jarvis, and D. Anthony Gray. "Trichloroethylene." In Handbook of Environmental Fate and Exposure Data For Organic Chemicals, Volume II, 467–74. Boca Raton: CRC Press, 2023. http://dx.doi.org/10.1201/9781003418863-73.

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Wartenberg, Daniel, and Kathleen M. Gilbert. "Trichloroethylene and Cancer." In Trichloroethylene: Toxicity and Health Risks, 171–84. London: Springer London, 2014. http://dx.doi.org/10.1007/978-1-4471-6311-4_9.

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Reisfeld, Brad, and Jaime H. Ivy. "Mathematical Modeling and Trichloroethylene." In Trichloroethylene: Toxicity and Health Risks, 209–37. London: Springer London, 2014. http://dx.doi.org/10.1007/978-1-4471-6311-4_11.

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Cooney, Craig A. "Epigenetic Alterations due to Trichloroethylene." In Trichloroethylene: Toxicity and Health Risks, 185–208. London: Springer London, 2014. http://dx.doi.org/10.1007/978-1-4471-6311-4_10.

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Doherty, Richard E. "History of TCE." In Trichloroethylene: Toxicity and Health Risks, 1–14. London: Springer London, 2014. http://dx.doi.org/10.1007/978-1-4471-6311-4_1.

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Gilbert, Kathleen M. "Trichloroethylene and Autoimmunity in Human and Animal Models." In Trichloroethylene: Toxicity and Health Risks, 15–35. London: Springer London, 2014. http://dx.doi.org/10.1007/978-1-4471-6311-4_2.

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Conference papers on the topic "Trichloroethylene"

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Ungureanu, Costica, and Valer Almasan. "Infrared multiphoton absorption of trichloroethylene isotopic species." In ROMOPTP '94: 4th Conference on Optics, edited by Valentin I. Vlad. SPIE, 1995. http://dx.doi.org/10.1117/12.203535.

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Kornhauser, Alan A. "Aqua-Ammonia as an Environmentally Acceptable Low Temperature Brine." In ASME 2011 International Mechanical Engineering Congress and Exposition. ASMEDC, 2011. http://dx.doi.org/10.1115/imece2011-62684.

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In many industrial processes, cooling with brines is preferable to cooling with an evaporating refrigerant. For medium and high temperatures (above about −35°C/−30°F), aqueous solutions of calcium chloride, sodium chloride, ethylene glycol, propylene glycol, and methanol have typically been used. For very low temperatures (down to about −80°C/-110°F) halocarbon refrigerants methylene chloride and trichloroethylene have generally been used. In recent years, both methylene chloride and trichloroethylene have come under increasingly strict regulation because of their toxicity. While many plants continue to use these brines, most are searching for alternates. This study was begun in response to the needs of a plant that was replacing methylene chloride with aqueous calcium chloride. The high viscosity of the calcium chloride brine caused design and operational problems. The above-mentioned brines, as well as aqua-ammonia, polydimethylsiloxane, and d-limonene, were compared for cost, toxicity, flammability, environmental safety, and energy efficiency. The energy efficiency comparison included comparisons of heat transfer coefficient, mass flow rate, volume flow rate, frictional pressure drop, inertial pressure drop, and pumping power. The comparisons indicated that aqua-ammonia was the best choice as a replacement for methylene chloride and trichloroethylene in some temperature ranges.
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Hsiao, M. C., B. T. Merritt, B. M. Penetrante, G. E. Vogtlin, and P. H. Wallman. "Pulsed corona and dielectric-barrier discharge processing of trichloroethylene." In International Conference on Plasma Science (papers in summary form only received). IEEE, 1995. http://dx.doi.org/10.1109/plasma.1995.533499.

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Angel, S. M., Kevin C. Langry, Jeffrey N. Roe, Bill W. Colston, Jr., Paul F. Daley, and Fred P. Milanovich. "Preliminary field demonstration of a fiber optic trichloroethylene sensor." In Microlithography '91, San Jose,CA, edited by Robert A. Lieberman and Marek T. Wlodarczyk. SPIE, 1991. http://dx.doi.org/10.1117/12.24802.

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Ungureanu, Costica, and M. Ungureanu. "Infrared photochemistry of trichloroethylene in the presence of oxygen." In ROMOPTO '97: Fifth Conference on Optics, edited by Valentin I. Vlad and Dan C. Dumitras. SPIE, 1998. http://dx.doi.org/10.1117/12.312814.

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Fen, Chiu-Shia, and Po-Yang Yen. "Transport of Trichloroethylene Vapor in a Dry Soil Column." In The 3rd World Congress on Civil, Structural, and Environmental Engineering. Avestia Publishing, 2018. http://dx.doi.org/10.11159/awspt18.103.

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Roberts, Jeffery J., and Dorthe Wildenschild. "Electrical Properties of Sand‐Clay Mixtures Containing Trichloroethylene and Ethanol." In Symposium on the Application of Geophysics to Engineering and Environmental Problems 2002. Environment and Engineering Geophysical Society, 2002. http://dx.doi.org/10.4133/1.2927169.

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Hu, Wei, Luoping Zhang, Christopher Kim, Xiaojiang Tang, Sungkyoon Kim, Bryan Bassig, Wei-Jie Seow, et al. "Abstract 840: Occupational exposure to trichloroethylene and LINE-1 methylation." In Proceedings: AACR 106th Annual Meeting 2015; April 18-22, 2015; Philadelphia, PA. American Association for Cancer Research, 2015. http://dx.doi.org/10.1158/1538-7445.am2015-840.

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J. Roberts, Jeffery, and Dorthe Wildenschild. "Electrical Properties Of Sand–Clay Mixtures Containing Trichloroethylene And Ethanol." In 15th EEGS Symposium on the Application of Geophysics to Engineering and Environmental Problems. European Association of Geoscientists & Engineers, 2002. http://dx.doi.org/10.3997/2214-4609-pdb.191.12pet3.

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Vandenbroucke, A. M., A. Vanderstricht, M. T. Nguyen Dinh, J. M. Giraudon, R. Morent, N. De Geyter, J. F. Lamonier, and C. Leys. "Non-thermal plasma abatement of trichloroethylene with DC corona discharges." In AIR POLLUTION 2011. Southampton, UK: WIT Press, 2011. http://dx.doi.org/10.2495/air110331.

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Reports on the topic "Trichloroethylene"

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Steel-Goodwin, Linda, and Alasdair J. Carmichael. Trichloroethylene Radicals: An EPR/SPIN Trapping Study. Fort Belvoir, VA: Defense Technical Information Center, July 1995. http://dx.doi.org/10.21236/ada361037.

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Phelps, T. J., D. Ringelberg, A. T. Mikell, D. C. White, and C. B. Fliermans. Mineralization of trichloroethylene by heterotrophic enrichment cultures. Office of Scientific and Technical Information (OSTI), December 1988. http://dx.doi.org/10.2172/666263.

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Plumlee, K. E. Test Pile Reactivity Loss Due to Trichloroethylene. Office of Scientific and Technical Information (OSTI), March 2001. http://dx.doi.org/10.2172/780115.

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Thevenin, E., and J. McMillian. Trichloroethylene toxicity in a human hepatoma cell line. Office of Scientific and Technical Information (OSTI), December 1994. http://dx.doi.org/10.2172/121308.

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Holt, R. D. Physical properties of contaminated trichloroethylene and 1,1,1- trichloroethane. Office of Scientific and Technical Information (OSTI), October 1990. http://dx.doi.org/10.2172/6455568.

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Goltz, Mark N. Bioenhanced In-well Vapor Stripping (BEHIVS) to Treat Trichloroethylene. Fort Belvoir, VA: Defense Technical Information Center, February 2003. http://dx.doi.org/10.21236/ada438872.

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Rick Colwell, Corey Radtke, Mark Delwiche, Deborah Newby, Lynn Petzke, Mark Conrad, Eoin Brodie, et al. Coupled Biogeochemical Process Evaluation for Conceptualizing Trichloroethylene Co-Metabolism. Office of Scientific and Technical Information (OSTI), June 2006. http://dx.doi.org/10.2172/896426.

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Wilkinson, Donald R., Earl Benjamin, and Lisa Imbrogno. The Effect of Metallic Ions on Trichloroethylene Degradation in Soils. Fort Belvoir, VA: Defense Technical Information Center, July 1999. http://dx.doi.org/10.21236/ada585149.

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Jerome, K. M. Diffusion of trichloroethylene through the threaded joints of PVC (polyvinylchloride) pipe. Office of Scientific and Technical Information (OSTI), December 1990. http://dx.doi.org/10.2172/6326686.

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Crawford, Ronald L., and Andrzej J. Paszczynski. Final Progress Report: Coupled Biogeochemical Process Evaluation for Conceptualizing Trichloroethylene Cometabolism. Office of Scientific and Technical Information (OSTI), February 2010. http://dx.doi.org/10.2172/972214.

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