Kinetics of Absorption of Nitric Oxide in Hydrogen Peroxide Solutions

Total Page:16

File Type:pdf, Size:1020Kb

Kinetics of Absorption of Nitric Oxide in Hydrogen Peroxide Solutions tional pressure drop were in approximate agreement radius of gas passage, rw-b [cm] with the theoretical predictions for the case of no rw columnradius [cm] ScG gas-phase Schmidt number, /uG/PGDG [-] rippling liquid film. ShG average gas-phase Sherwood number, Experiments on the absorption of ammoniafrom a [-] turbulent air stream into aqueous sulfuric acid solu- u average gas velocity [cm/sec] tion were carried out under the conditions of rippling ut interfacial velocity [cm/s ec] on the surface of the liquid film. The agreement be- W mass flow rate of gas [g/s ec] X = dimensionless column height, Z/2r* [-] tween the measured values of ShGand the theoretical z = column height [cm] predictions for the case of no rippling liquid film was fairly good. r = mass flow rate of liquid per unit perimeter From these results, it may be concluded that rippling [g/cm - sec] on the surface of the falling liquid film does not affect APf = frictional pressure drop for gas stream through column [g/cm à" sec2] or [Kg-force/m2] appreciably either the frictional pressure drop or the fjLG9fiL = viscosities of gas and liquid [g/cm-sec] or [cP] rate of gas-phase mass transfer in the turbulent gas pG = density of gas [g/cm3] stream. Literature Cited b Nomenclature 1) Emmert, R. E. and R. L. Pig ford: Chem. Eng. Progr., 50, = liquid film thickness [cm] 87 (1954). DG = gas-phase diffusivity of solute gas [cm2/sec] 2) Hikita, H.: Kagaku Kogaku, 23, 23 (1959). d = column diameter, 2rw [cm] 3) Hikita, H., K. Ishimi and H. Ikeki: /. Chem. Eng. Japan, fr = friction factor based on relative gas 10, 375 (1977). velocity, APfrilpG{um - uifZ [-] 4) Hikita, H., K. Ishimi, Y. Omotehara and T. Fukase: ibid., average gas-phase mass transfer coefficient ll, 96 (1978). [cm/s ec] 5) Kafesjian, R. L., C. A. Plank and E. R. Gerhard: AIChE gas-phase Reynolds number, A W]izdiiG [-] /., 7, 463 (1961). gas-phase Reynolds number based on 6) Kamei, S. and J. Oishi: Kagaku Kogaku, 18, 421 (1954). gas velocity relative to liquid surface, 7) Malyusov, V.A., S.K. Myasnikov and N.N. Kulov: 2riPG(um - Ui)/^G [-] Theor. Found. Chem. Eng., 1, 480 (1973). ReL = liquid-phase Reynolds number, 4r//jtL [-] KINETICS OF ABSORPTION OF NITRIC OXIDE IN HYDROGEN PEROXIDE SOLUTIONS K. K. BAVEJA, D. SUBBA RAO and M. K. SARKAR Department of Chemical Engineering, Indian Institute of Technology, Hauz Khas, NewDelhi-110029 India Introduction cost and formation of only water and nitric acid in the absorption process. This last factor makes it Absorption is a useful technique for removal of specially attractive for nitric acid plant tail-gas ab- nitric oxide from a gas mixture in many applications. sorption, since the by-product from air pollution A number of absorbents have been proposed for the removal of NOfrom gases. Adrian et al.l) have abatement can go directly into the main product of reported on the development of a process for the the plant. There is practically no information in the literature reduction of NOcontent in flue gases using hydrogen on the kinetics of the reaction between H2O2 and peroxide solution as the absorbing liquid. Absorp- NOin the liquid phase. As a first step, an attempt tion with hydrogen peroxide solution has considerable is made to elucidate the kinetics of absorption of advantages, such as high absorption rate, low capital NOin hydrogen peroxide solution and to determine Received October 13, 1978. Correspondence concerning this article should beaddressed to M. K. Sarkar. the rate constant. The overall reaction with NOis 322 JOURNAL OF CHEMICAL ENGINEERING OF JAPAN 2 NO+3 H2O2-+2 HNO3+2H2O preliminary runs on the physical absorption of pure CO2in water were carried out in the sameapparatus 1. Experimental at stirrer speeds of 61 and 100 rpm to determine kL9 Absorption experiments were carried out in a the liquid-side physical mass transfer coefficient. 10.15 cm I. D. glass stirred cell with a total volume 2. Theory of approximately 1 litre. The design of the stirred cell was similar to that used by Ladhabhoy and The theory of absorption accompanied by fast Sharma4). The top part was provided with one B-24 pseudo-m-th order reaction is applied to this system. and two B-l4joints. The stirrer shaft passed through For a reaction m-th order with respect to the gaseous a mercury seal through the central B-24 joint. The reactant A (NO) and n-th order with respect to the B-l4 joints were used to connect gas inlet and gas liquid reactant B (H2O2), the specific rate of gas absorption according to the film theory can be ex- outlet tubes. A glass stirrer with two sets of four pressed in terms of enhancement factor E by an flat blades spaced about 8 mmapart was used. During the experiment, the liquid level was maintained in the approximate solution2) : middle of the two sets of blades, so that one set causes stirring in the liquid phase and the other in |pf] /tanh^f^f] (1) the gas phase. The effective inter facial area in the where stirred cell was 81 cm2. E=RAIA*kL (2) Two stirrer speeds viz. 61 rpm and 100 rpm, were used in the experiments. At both these speeds the </MA =1-. liquid surface was observed to be quite smooth. m+\-DAkU^r-KBoT (3) The absorbing liquid used was an aqueous solution and of H2O2 having a concentration in the range of Ei=enhancement factor when the reaction is instan- 1.07X10"4 to 5.66X10"4 g-mol/cm3. The solute gas taneous, or rate of reaction is controlled entirely NO, suitably diluted with N2 and saturated with by diffusion water vapour, was fed into the absorber at a constant = 1 +V>bBo)/(zDaA*) (4) rate. The concentration of NO in the feed gas The above equations are applicable when the concen- ranged from 7 to 25vol%. The total pressure in tration of the gaseous component in the bulk liquid the system was 740mmof mercury, which is the (Ao) is zero. localBatchatmosphericexperimentspressure.were conducted by taking a When knownvolume of hydrogen peroxide solution (280 then E= *JW~A cm3) in the cell and purging the system first with and therefore nitrogen and then with the gas consisting of desired Ra=J concentration of NOin N2. The duration of the m+lDAkmnu(V) *y+l{Boy experimental run was 20 minutes. Hydrogen perox- ide concentration was measured iodometrically at The conditions given by expression (5) were satisfied the beginning and at the end of the experimental in all the results reported and are discussed later. run6). The change in solution concentration never These conditions also justify the assumption AQ=0. exceeded 8%of the initial value. The mean of the Further, if Eq. (7) is valid, the specific rate of absorp- two values was taken as the average H2O2 concen- tion should be independent of kL and hence of the tration. The concentration of NOin inlet and outlet speed of stirring. gas samples from the absorber was determined by gas chromatography using Molecular Sieve 13X 3. Results and Discussion as the columnpacking. The gas phase was assumed 3. 1 Evaluation of parameters to be completely back-mixed and the outlet gas con- The solubility and dirBsivity of nitric oxide in the centration wastaken as the representative gas con- reacting solution was taken to be same as that in centration in the cell. The amount of NOabsorbed water because of the low concentration of hydrogen during the experimental run was calculated from the peroxide used and of HNO3formed. The maximum acid formed in liquid and determined titrimetrically. concentration of HNO3formed in any experiment This was also checked in a few experiments by calcu- in 20minutes was 1.4x10"5 g-mol/cm3. The solu- lating the amount of NOabsorbed from the inlet bility data at 1 atmosphere pressure was taken from and outlet gas analysis, and the material balance was Perry5) and corrected for pressure. The diffusivity found to agree within 4%. data was taken from Hikita et a/.3). In view ofthelow Prior to the chemical absorption experiments, solubility of nitric oxide in the solution at the reaction VOL 12 NO.4 1979 323 Fig. 1 Effect ofA* on specific rate of absorption Fig4. Effect of temperature on reaction rate RA, 30°C constant k2 experiments. 3. 2 Confirmation of regime Experiments on specific rate of absorption were carried out at stirrer speeds of 61 and 100rpm. The value of physical mass transfer coefficient at these stirrer speeds was independently found to be 1.7x lO~3 and 2.6X 10"3 cm/sec respectively. How- ever, the specific rate of absorption of NOin H2O2 was found to be independent of the speed of stirring. For the range of experiments conducted at 61 rpm, the value of E was found to vary between 30 and 65. For DA=DBand f^>l, Eq. (4) can be approxi- mated by Ei =B0/zA* (8) Fig. 2 Effect of Bo on specific rate of absorption RA, ,4*=4.0 X 10-7 g-mol/cm3, 30°C The values of B0/zA* varied from approximately 205 to 2,100. The ratio DA/DBis very likely to be close to unity. The values of E (and hence VMA)and Bo/zA* were evaluated individually for each ex- periment to ensure that conditions given by expression (5) are satisfied. 3. 3 Discussion of results The effect of A* on specific rate of absorption was studied for four different liquid concentrations, keep- ing stirrer speed at 61 rpm at 30°C.
Recommended publications
  • The Decomposition Kinetics of Peracetic Acid and Hydrogen Peroxide in Municipal Wastewaters
    Disinfection Forum No 10, October 2015 The Decomposition Kinetics of Peracetic Acid and Hydrogen Peroxide in Municipal Wastewaters INTRODUCTION Efficient control of microbial populations in municipal wastewater using peracetic acid (PAA) requires an understanding of the PAA decomposition kinetics. This knowledge is critical to ensure the proper dosing of PAA needed to achieve an adequate concentration within the contact time of the disinfection chamber. In addition, the impact of PAA on the environment, post-discharge into the receiving water body, also is dependent upon the longevity of the PAA in the environment, before decomposing to acetic acid, oxygen and water. As a result, the decomposition kinetics of PAA may have a significant impact on aquatic and environmental toxicity. PAA is not manufactured as a pure compound. The solution exists as an equilibrium mixture of PAA, hydrogen peroxide, acetic acid, and water: ↔ + + Acetic Acid Hydrogen Peroxide Peracetic Acid Water PeroxyChem’s VigorOx® WWT II Wastewater Disinfection Technology contains 15% peracetic acid by weight and 23% hydrogen peroxide as delivered. Although hydrogen peroxide is present in the formulation, peracetic acid is considered to be the active component for disinfection1 in wastewater. There have been several published studies investigating the decomposition kinetics of PAA in different water matrices, including municipal wastewater2-7. Yuan7 states that PAA may be consumed in the following three competitive reactions: 1. Spontaneous decomposition 2 CH3CO3H à 2 CH3CO2H + O2 Eq (1) 2. Hydrolysis CH3CO3H + H2O à CH3CO2H + H2O2 Eq (2) 3. Transition metal catalyzed decomposition + CH3CO3H + M à CH3CO2H + O2 + other products Eq (3) At neutral pH’s, both peracetic acid and hydrogen peroxide can be rapidly consumed by these reactions7 (hydrogen peroxide will decompose to water and oxygen via 2H2O2 à 2H2O + O2).
    [Show full text]
  • University of Groningen Discovery of a Eugenol Oxidase From
    University of Groningen Discovery of a eugenol oxidase from Rhodococcus sp strain RHA1 Jin, J.F.; Mazon, H.; van den Heuvel, R.H.H.; Janssen, D.B.; Fraaije, M.W. Published in: Febs Journal DOI: 10.1111/j.1742-4658.2007.05767.x IMPORTANT NOTE: You are advised to consult the publisher's version (publisher's PDF) if you wish to cite from it. Please check the document version below. Document Version Publisher's PDF, also known as Version of record Publication date: 2007 Link to publication in University of Groningen/UMCG research database Citation for published version (APA): Jin, J. F., Mazon, H., van den Heuvel, R. H. H., Janssen, D. B., & Fraaije, M. W. (2007). Discovery of a eugenol oxidase from Rhodococcus sp strain RHA1. Febs Journal, 274(9), 2311 - 2321. https://doi.org/10.1111/j.1742-4658.2007.05767.x Copyright Other than for strictly personal use, it is not permitted to download or to forward/distribute the text or part of it without the consent of the author(s) and/or copyright holder(s), unless the work is under an open content license (like Creative Commons). Take-down policy If you believe that this document breaches copyright please contact us providing details, and we will remove access to the work immediately and investigate your claim. Downloaded from the University of Groningen/UMCG research database (Pure): http://www.rug.nl/research/portal. For technical reasons the number of authors shown on this cover page is limited to 10 maximum. Download date: 23-09-2021 Discovery of a eugenol oxidase from Rhodococcus sp.
    [Show full text]
  • Algorithmic Analysis of Chemical Dynamics of the Autoignition of NH3–H2O2/Air Mixtures
    energies Article Algorithmic Analysis of Chemical Dynamics of the Autoignition of NH3–H2O2/Air Mixtures Ahmed T. Khalil 1,2, Dimitris M. Manias 3, Efstathios-Al. Tingas 4, Dimitrios C. Kyritsis 1,2,* and Dimitris A. Goussis 1,2 1 Department of Mechanical Engineering, Khalifa University of Science and Technology, Abu Dhabi 127788, UAE; [email protected] (A.T.K.); [email protected] (D.A.G.) 2 Research and Innovation Center on CO2 and H2 (RICH), Khalifa University of Science and Technology, P.O. Box 127788, Abu Dhabi, UAE 3 Department of Mechanics, School of Applied Mathematics and Physical Sciences, National Technical University of Athens, 157 73 Athens, Greece; [email protected] 4 Perth College, University of the Highlands and Islands, (UHI), Perth PH1 2NX, UK; [email protected] * Correspondence: [email protected] Received: 8 September 2019; Accepted: 7 October 2019; Published: 21 November 2019 Abstract: The dynamics of a homogeneous adiabatic autoignition of an ammonia/air mixture at constant volume was studied, using the algorithmic tools of Computational Singular Perturbation. Since ammonia combustion is characterized by both unrealistically long ignition delays and elevated NOx emissions, the time frame of action of the modes that are responsible for ignition was analyzed by calculating the developing time scales throughout the process and by studying their possible relation to NOx emissions. The reactions that support or oppose the explosive time scale were identified, along with the variables that are related the most to the dynamics that drive the system to an explosion.
    [Show full text]
  • Interaction of Ozone and Hydrogen Peroxide in Water Implications For
    UC Irvine Faculty Publications Title Interaction of ozone and hydrogen peroxide in water: Implications for analysis of H 2 O 2 in air Permalink https://escholarship.org/uc/item/7j7454z7 Journal Geophysical Research Letters, 9(3) ISSN 00948276 Authors Zika, R. G Saltzman, E. S Publication Date 1982-03-01 DOI 10.1029/GL009i003p00231 License https://creativecommons.org/licenses/by/4.0/ 4.0 Peer reviewed eScholarship.org Powered by the California Digital Library University of California GEOPHYSICLARESEARCH LETTERS, VOL. 9, NO. 3, PAGES231-234 , MARCH1982 INTERACTION OF OZONE AND HYDROGEN PEROXIDE IN WATER: IMPLICATIONSFORANALYSIS oFH20 2 IN AIR R.G. Zika and E.S. Saltzman Division of Marine and Atmospheric Chemistry, University of Miami, Miami, Florida 331#9 Abstract. We have attempted to measure gaseous Analytical Methods H202 in air usingan aqueoustrapping method. With continuousbubbling, H 20 2 levels in the traps reacheda a. Hydrogen Peroxide. Hydrogen peroxide in aqueous plateau, indicating that a state of dynamic equilibrium solution was measured using a modified fluorescence involving H202 destrbction was established. We decay technique [Perschke and Broda, 1976; Zika and attribute this behavior to the interaction of ozone and its Zelmer, 1982]. The method involved the addition of a decompositionproducts (OH, O[) withH 20 2 inacld:•ous known amot•at of scopoletin (6-methyl-7-hydroxyl-i,2- solution. This hypothesis was investigated by replacing benzopyrone)to a pH 7.0 phosphatebuffered. sample. the air stream with a mixture of N2, 02 and 0 3. The The sample was prepared bY diluting an aliquot of the results Of this experiment show that H O was both reaction solution to 20 mls with low contaminant producedand destroyedin the traps.
    [Show full text]
  • Hydrogen Peroxide Cas #7722-84-1
    HYDROGEN PEROXIDE CAS #7722-84-1 Division of Toxicology ToxFAQsTM April 2002 This fact sheet answers the most frequently asked health questions (FAQs) about hydrogen peroxicde. For more information, call the ATSDR Information Center at 1-888-422-8737. This fact sheet is one in a series of summaries about hazardous substances and their health effects. It is important you understand this information because this substance may harm you. The effects of exposure to any hazardous substance depend on the dose, the duration, how you are exposed, personal traits and habits, and whether other chemicals are present. HIGHLIGHTS: Hydrogen peroxide is a manufactured chemical, although small amounts of hydrogen peroxide gas may occur naturally in the air. Low exposure may occur from use at home; higher exposures may occur from industrial use. Exposure to hydrogen peroxide can cause irritation of the eyes, throat, respiratory airway, and skin. Drinking concentrated liquid can cause mild to severe gastrointestinal effects. This substance has been found in at least 18 of the 1,585 National Priorities List sites identified by the Environmental Protection Agency (EPA). What is hydrogen peroxide? ‘ If released to soil, hydrogen peroxide will be broken down Hydrogen peroxide is a colorless liquid at room temperature by reacting with other compounds. with a bitter taste. Small amounts of gaseous hydrogen peroxide occur naturally in the air. Hydrogen peroxide is ‘ Hydrogen peroxide does not accumulate in the food chain. unstable, decomposing readily to oxygen and water with release of heat. Although nonflammable, it is a powerful How might I be exposed to hydrogen peroxide? oxidizing agent that can cause spontaneous combustion when it comes in contact with organic material.
    [Show full text]
  • Production of Hydrogen Peroxide from Carbon Monoxide, Water and Oxygen Over Alumina-Supported Ni Catalysts
    _______________________________________________________________________________www.paper.edu.cn Journal of Molecular Catalysis A: Chemical 210 (2004) 157–163 Production of hydrogen peroxide from carbon monoxide, water and oxygen over alumina-supported Ni catalysts Zhong-Long Ma, Rong-Li Jia, Chang-Jun Liu∗ Key Laboratory of Green Synthesis and Transformation of Ministry of Education, School of Chemical Engineering and Technologies, Tianjin University, Tianjin 300072, PR China Received 23 April 2003; accepted 11 September 2003 Abstract Novel amorphous Ni–B catalysts supported on alumina have been developed for the production of hydrogen peroxide from carbon monoxide, water and oxygen. The experimental investigation confirmed that the promoter/Ni ratio and the preparation conditions have a significant effect on the activity and lifetime of the catalyst. Among all the catalysts tested, the Ni–La–B/␥-Al2O3 catalyst with a 1:15 atomic ratio of La/Ni, dried at 120 ◦C, shows the best activity and lifetime for the production of hydrogen peroxide. The deactivation of the alumina-supported Ni–B amorphous catalyst was also studied. According to the characterizations of the fresh and used catalysts by SEM, XRD and XPS, no sintering of the active component and crystallization of the amorphous species were observed. However, it is water poisoning that leads to the deactivation of the catalyst. The catalyst characterization demonstrated that the active component had changed (i.e., amorphous NiO to amorphous Ni(OH)2) and then salt was formed in the reaction conditions. Water promoted the deactivation because the surface transformation of the active Ni species was accelerated by forming Ni(OH)2 in the presence of water.
    [Show full text]
  • Hydrogen Peroxide Oxidation of Aromatic Hydrocarbons by Immobilized Iron(III)
    Journal of Molecular Catalysis A: Chemical 217 (2004) 161–164 Hydrogen peroxide oxidation of aromatic hydrocarbons by immobilized iron(III) Hassan Hosseini Monfared∗, Zahra Amouei Department of Chemistry, School of Sciences, Zanjan University, Zanjan 45195-313, Iran Received 30 October 2003; received in revised form 16 March 2004; accepted 16 March 2004 Available online 27 April 2004 Abstract Supported iron(III) ions on neutral ␥-alumina are an efficient catalyst for the oxidation of aromatic hydrocarbons with hydrogen peroxide in acetonitrile at 60 ◦C. The catalyst is active in the low temperatue liquid phase oxidation of benzene, toluene, chlorobenzene, p-xylene, mesitylene, benzaldehyde with hydrogen peroxide. Conversions of 31–88% with respect to starting substrate were obtained within 6 h. Oxidation on both the side chain and the aromatic ring of hydrocarbons occurred. © 2004 Elsevier B.V. All rights reserved. Keywords: Aromatic hydrocarbons; Hydrogen peroxide; Heterogeneous catalyst; Oxidation 1. Introduction ions on silica [4] or alumina [5], considerably retards the non-productive decomposition of H2O2. Here, we report that The selective catalytic oxidation of organic molecules supported iron ions on ␥-alumina show remarkable catalytic continues to be a very important method for the prepara- properties in activation of H2O2 for aromatic hydrocarbons tion of primary and specialty chemicals in the chemical oxidation. industry worldwide. Catalytic oxidation reactions using metal complexes are valuable for facilitation the devel- opment
    [Show full text]
  • Use of Hydrogen Peroxide for Coronavirus Disinfection Dennis Wolf, MTAS Fire Management Consultant | April 17, 2020
    Use of Hydrogen Peroxide for Coronavirus Disinfection Dennis Wolf, MTAS Fire Management Consultant | April 17, 2020 MTAS received an inquiry about the use of hydrogen peroxide as a disinfecting agent for the coronavirus as an option to bleach because of bleach’s corrosive potential and irritating odor. MTAS researched this question and provides the following information. MTAS does not recommend or endorse any product, and the products mentioned here are for illustration only. MTAS recommends that municipalities do their own research and select products and procedures that meet local needs. The most common form of hydrogen peroxide available is a 3% concentration in a dark plastic bottle at a pharmacy or other store. Currently, 3% hydrogen peroxide may be difficult to find due to high demand. There is another form of hydrogen peroxide called accelerated hydrogen peroxide (AHP). This is a synergistic mixture of hydrogen peroxide, surfactants, and inert ingredients which results in a stabilized disinfectant that is more effective than plain hydrogen peroxide. The benefits of AHP over 3% hydrogen peroxide include better cleaning efficiency and a shorter dwell, or contact, time for the product to remain on the surface. The product must remain on the surface of the item being cleaned and decontaminated long enough for the hydrogen peroxide to kill whatever pathogens are present. The coronavirus is an enveloped virus, which is a type of virus that is susceptible to hydrogen peroxide. With proper application and dwell time, both 3% hydrogen peroxide and accelerated hydrogen peroxide will kill the coronavirus to a rate of at least 99.9%.
    [Show full text]
  • In Vitro Evaluation of the Whitening Effect of Mouth Rinses Containing Hydrogen Peroxide
    Aesthetic Dentistry Restorative Dentistry In vitro evaluation of the whitening effect of mouth rinses containing hydrogen peroxide Abstract: The aim of this study was to evaluate the bleaching effect of two mouth rinses containing hydrogen peroxide. Thirty premolars were randomly Fábio Garcia Lima(a) Talita Aparecida Rotta(b) divided into two groups (n = 15): Listerine Whitening (LW) and Colgate Plax Sonara Penso(b) Whitening (PW). The teeth were fixed on a wax plate and with acrylic resin, (c) Sônia Saeger Meireles at a distance of 5 mm between each other, exposing the buccal surfaces. All Flávio Fernando Demarco(a) teeth were stored in artificial saliva for 45 days, being removed twice a day to be immersed for 1 min in each mouthwash, followed by 10-second wash- (a) Department of Restorative Dentistry, School ing in tap water. The pH of each product was measured. Digital images of of Dentistry, Federal University of Pelotas, each tooth were captured under standardized conditions. These images were Pelotas, RS, Brazil. cut in areas previously demarcated and analyzed in Adobe Photoshop 7.0 us- (b) Private practice, Joaçaba, SC, Brazil. ing the CIEL*a*b* color space system. Data were statistically analyzed by a (c) Department of Restorative Dentistry, School paired t test and an independent samples t test (p < 0.05). The pH values were of Dentistry, Federal University of João 5.6 and 3.4 for LW and PW, respectively. Both treatment groups showed a de- Pessoa, João Pessoa, PB, Brazil. crease in the b* parameter (p < 0.01), but a decrease of a* was observed only for PW (p < 0.01).
    [Show full text]
  • ADA Conditions for Acceptance the Bases for Review of All Toothpastes
    ADA Conditions For Acceptance The bases for review of all toothpastes submitted to the ADA Acceptance Program are the Guidelines for Fluoride-Containing Dentifrices. These guidelines detail the testing required to demonstrate that the dentifrice is safe and effectively prevents caries. In addition to this testing, whitening toothpastes are evaluated according to the ADA Acceptance Program Guidelines for Home-Use Tooth Whitening Products. Any other therapeutic claim attributed to whitening tooth- pastes also must be supported with studies (for example, claims for the reduction of plaque and gingivitis or hypersensitivity should be supported by studies consistent with ADA guidelines). ADA consultants review the testing results supplied by the tooth-paste manufacturers. ADA Approved Whitening Toothpaste Crest Extra Whitening with Tartar Protection Toothpaste (Received ADA Seal of Acceptance in September 1999) Crest Multicare Whitening Toothpaste (February 2000) Colgate Tartar Control Plus Whitening Gel (March 2000) Aquafresh Whitening Tooth-paste (April 2000) Colgate Total Plus Whitening Toothpaste (June 2000) Rembrandt Whitening Toothpaste (October 2000) What are in These Toothpastes Abrasives (to remove debris and residual stain) Humectants (to prevent loss of water) Thickening Agents or Binders (to stabilize tooth-paste formulations and prevent separation of liquid and solid phases) Flavoring and Foaming Agents (a preference of consumers) Therapeutic Agents Fluoride (Contained in all ADA-Accepted toothpastes for reducing caries) Potassium Nitrate (To treat dentinal hypersensitivity) Triclosan or Stannous Fluoride (To reduce gingival inflammation) Other agents that may be added to toothpastes to provide esthetic benefits Pyrophosphates or Zinc Citrate (To prevent tartar buildup) Various Abrasives or Enzymes (To help whiten teeth) Toothpastes that whiten teeth work by chemically or mechanically removing stain.
    [Show full text]
  • DE Medicaid MAC List Effective As of 1/5/2018
    OptumRx - DE Medicaid MAC List Effective as of 1/5/2018 Generic Label Name & Drug Strength Effective Date MAC Price OTHER IV THERAPY (OTIP) 10/25/2017 77.61750 PENICILLIN G POTASSIUM FOR INJ 5000000 UNIT 3/15/2017 8.00000 PENICILLIN G POTASSIUM FOR INJ 20000000 UNIT 3/15/2017 49.62000 PENICILLIN G SODIUM FOR INJ 5000000 UNIT 10/25/2017 53.57958 PENICILLIN V POTASSIUM TAB 250 MG 1/3/2018 0.05510 PENICILLIN V POTASSIUM TAB 500 MG 12/29/2017 0.10800 PENICILLIN V POTASSIUM FOR SOLN 125 MG/5ML 10/26/2017 0.02000 PENICILLIN V POTASSIUM FOR SOLN 250 MG/5ML 12/22/2017 0.02000 AMOXICILLIN (TRIHYDRATE) CAP 250 MG 12/22/2017 0.03930 AMOXICILLIN (TRIHYDRATE) CAP 500 MG 11/1/2017 0.05000 AMOXICILLIN (TRIHYDRATE) TAB 500 MG 12/28/2017 0.20630 AMOXICILLIN (TRIHYDRATE) TAB 875 MG 10/31/2017 0.08000 AMOXICILLIN (TRIHYDRATE) CHEW TAB 125 MG 10/26/2017 0.12000 AMOXICILLIN (TRIHYDRATE) CHEW TAB 250 MG 10/26/2017 0.24000 AMOXICILLIN (TRIHYDRATE) FOR SUSP 125 MG/5ML 10/28/2017 0.00667 AMOXICILLIN (TRIHYDRATE) FOR SUSP 200 MG/5ML 12/20/2017 0.01240 AMOXICILLIN (TRIHYDRATE) FOR SUSP 250 MG/5ML 12/18/2017 0.00980 AMOXICILLIN (TRIHYDRATE) FOR SUSP 400 MG/5ML 12/28/2017 0.01310 AMPICILLIN CAP 250 MG 9/26/2017 0.07154 AMPICILLIN CAP 500 MG 11/6/2017 0.24000 AMPICILLIN FOR SUSP 125 MG/5ML 3/17/2017 0.02825 AMPICILLIN FOR SUSP 250 MG/5ML 9/15/2017 0.00491 AMPICILLIN SODIUM FOR INJ 250 MG 3/15/2017 1.38900 AMPICILLIN SODIUM FOR INJ 500 MG 7/16/2016 1.02520 AMPICILLIN SODIUM FOR INJ 1 GM 12/20/2017 2.00370 AMPICILLIN SODIUM FOR IV SOLN 1 GM 7/16/2016 15.76300 AMPICILLIN
    [Show full text]
  • Hydrogen Peroxide Ear Drops
    Patient Information Hydrogen Peroxide Ear Drops Hydrogen Peroxide Ear Drops Recipe: • 3% Hydrogen Peroxide. This can be purchased from any chemist without needing a prescription. • 3-5ml syringe or a medicine dropper. When instilled in the ear you will feel a warm tingling sensation, and a bubbling/fizzing sound (sometimes described a little like ‘Rice-Bubbles’). This solution is safe in all ears even when you have grommets or an eardrum perforation. Using Eardrops: • Place your head on side. Use the syringe or dropper to fill up the ear with the solution (around 1-3 ml). • ‘Pump’ the solution within the ear canal using the ‘triangle’ of skin and cartilage in front to the ear canal for about 10-15sec. • Allow it to bubble and fizz. • Once you are used to the feeling the solution should be left to bubble and fizz in the ear for up to one minute at a time, although when you first use it you may only tolerate the feeling for a few seconds. • Tip solution out onto a tissue. • The ear canal will dry itself in the next minute or so. Use of Antibiotic Eardrops and Hydrogen Peroxide. The peroxide will damage the active ingredients in antibiotics. It is important that there is a 30min gap between hydrogen peroxide (best used first) and antibiotics. Frequency of Use: • If used for treatment of ear infections (outer or middle ear), please use three times a day in combination with the antibiotic drops prescribed by your doctor. Use the hydrogen peroxide first and allow a thirty minute gap between it and other drops.
    [Show full text]