5—Weak Acids, Bases and Their Salts
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Wastewater Technology Fact Sheet: Ammonia Stripping
United States Office of Water EPA 832-F-00-019 Environmental Protection Washington, D.C. September 2000 Agency Wastewater Technology Fact Sheet Ammonia Stripping DESCRIPTION Ammonia stripping is a simple desorption process used to lower the ammonia content of a wastewater stream. Some wastewaters contain large amounts of ammonia and/or nitrogen-containing compounds that may readily form ammonia. It is often easier and less expensive to remove nitrogen from wastewater in the form of ammonia than to convert it to nitrate-nitrogen before removing it (Culp et al., 1978). Ammonia (a weak base) reacts with water (a weak acid) to form ammonium hydroxide. In ammonia stripping, lime or caustic is added to the wastewater until the pH reaches 10.8 to 11.5 standard units which converts ammonium hydroxide ions to ammonia gas according to the following reaction(s): + - NH4 + OH 6 H2O + NH38 Source: Culp, et. al, 1978. Figure 1 illustrates two variations of ammonia FIGURE 1 TWO TYPES OF STRIPPING stripping towers, cross-flow and countercurrent. In TOWERS a cross-flow tower, the solvent gas (air) enters along the entire depth of fill and flows through the packing, as the alkaline wastewater flows it may be more economical to use alternate downward. A countercurrent tower draws air ammonia removal techniques, such as steam through openings at the bottom, as wastewater is stripping or biological methods. Air stripping may pumped to the top of a packed tower. Free also be used to remove many hydrophobic organic ammonia (NH3) is stripped from falling water molecules (Nutrient Control, 1983). droplets into the air stream, then discharged to the atmosphere. -
(Oxy)Hydroxide Electrocatalysts for Water Oxidation Bryan R
www.acsami.org Research Article Effect of Selenium Content on Nickel Sulfoselenide-Derived Nickel (Oxy)hydroxide Electrocatalysts for Water Oxidation Bryan R. Wygant, Anna H. Poterek, James N. Burrow, and C. Buddie Mullins* Cite This: ACS Appl. Mater. Interfaces 2020, 12, 20366−20375 Read Online ACCESS Metrics & More Article Recommendations *sı Supporting Information ABSTRACT: An efficient and inexpensive electrocatalyst for the oxygen evolution reaction (OER) must be found in order to improve the viability of hydrogen fuel production via water electrolysis. Recent work has indicated that nickel chalcogenide materials show promise as electrocatalysts for this reaction and that their performance can be further enhanced with the generation of ternary, bimetallic chalcogenides (i.e., Ni1−aMaX2); however, relatively few studies have investigated ternary chalcogenides created through the addition of a second chalcogen (i.e., NiX2−aYa). To address this, we fi studied a series of Se-modi ed Ni3S2 composites for use as OER electrocatalysts in alkaline solution. We found that the addition of Se results in the creation of Ni3S2/NiSe composites composed of cross-doped metal chalcogenides and show that the addition of 10% Se reduces the overpotential required to reach a current density of 10 mA/cm2 by 40 mV versus a pure nickel sulfide material. Chemical analysis of the composites’ surfaces shows a reduction in the amount of nickel oxide species with Se incorporation, which is supported by transmission electron microscopy; this reduction is correlated with a decrease in the OER overpotentials measured for these samples. Together, our results suggest that the incorporation of Se into Ni3S2 creates a more conductive material with a less-oxidized surface that is more electrocatalytically active and resistant to further oxidation. -
Choosing Buffers Based on Pka in Many Experiments, We Need a Buffer That Maintains the Solution at a Specific Ph. We May Need An
Choosing buffers based on pKa In many experiments, we need a buffer that maintains the solution at a specific pH. We may need an acidic or a basic buffer, depending on the experiment. The Henderson-Hasselbalch equation can help us choose a buffer that has the pH we want. pH = pKa + log([conj. base]/[conj. acid]) With equal amounts of conjugate acid and base (preferred so buffers can resist base and acid equally), then … pH = pKa + log(1) = pKa + 0 = pKa So choose conjugates with a pKa closest to our target pH. Chemistry 103 Spring 2011 Example: You need a buffer with pH of 7.80. Which conjugate acid-base pair should you use, and what is the molar ratio of its components? 2 Chemistry 103 Spring 2011 Practice: Choose the best conjugate acid-base pair for preparing a buffer with pH 5.00. What is the molar ratio of the buffer components? 3 Chemistry 103 Spring 2011 buffer capacity: the amount of strong acid or strong base that can be added to a buffer without changing its pH by more than 1 unit; essentially the number of moles of strong acid or strong base that uses up all of the buffer’s conjugate base or conjugate acid. Example: What is the capacity of the buffer solution prepared with 0.15 mol lactic acid -4 CH3CHOHCOOH (HA, Ka = 1.0 x 10 ) and 0.20 mol sodium lactate NaCH3CHOHCOO (NaA) and enough water to make 1.00 L of solution? (from previous lecture notes) 4 Chemistry 103 Spring 2011 Review of equivalence point equivalence point: moles of H+ = moles of OH- (moles of acid = moles of base, only when the acid has only one acidic proton and the base has only one hydroxide ion). -
Understanding Variation in Partition Coefficient, Kd, Values: Volume II
United States Office of Air and Radiation EPA 402-R-99-004B Environmental Protection August 1999 Agency UNDERSTANDING VARIATION IN PARTITION COEFFICIENT, Kd, VALUES Volume II: Review of Geochemistry and Available Kd Values for Cadmium, Cesium, Chromium, Lead, Plutonium, Radon, Strontium, Thorium, Tritium (3H), and Uranium UNDERSTANDING VARIATION IN PARTITION COEFFICIENT, Kd, VALUES Volume II: Review of Geochemistry and Available Kd Values for Cadmium, Cesium, Chromium, Lead, Plutonium, Radon, Strontium, Thorium, Tritium (3H), and Uranium August 1999 A Cooperative Effort By: Office of Radiation and Indoor Air Office of Solid Waste and Emergency Response U.S. Environmental Protection Agency Washington, DC 20460 Office of Environmental Restoration U.S. Department of Energy Washington, DC 20585 NOTICE The following two-volume report is intended solely as guidance to EPA and other environmental professionals. This document does not constitute rulemaking by the Agency, and cannot be relied on to create a substantive or procedural right enforceable by any party in litigation with the United States. EPA may take action that is at variance with the information, policies, and procedures in this document and may change them at any time without public notice. Reference herein to any specific commercial products, process, or service by trade name, trademark, manufacturer, or otherwise, does not necessarily constitute or imply its endorsement, recommendation, or favoring by the United States Government. ii FOREWORD Understanding the long-term behavior of contaminants in the subsurface is becoming increasingly more important as the nation addresses groundwater contamination. Groundwater contamination is a national concern as about 50 percent of the United States population receives its drinking water from groundwater. -
Proton Transfer Reaction in Water: Hydronium Ion Formation
Advanced Journal of Chemistry-Section A, 2020, 3(3), 255–258 Available online at : www.ajchem-a.com ISSN Online: 2645-5676 DOI: 10.33945/SAMI/AJCA.2020.3.2 Short Communication Proton Transfer Reaction in Water: Hydronium Ion Formation In Sang Leea, Sitansu Sekhar Nandab,* a Research Division, Divine Lab Limited, Seoul, South Korea b Department of Chemistry, Myongji University, Yongin, South Korea A R T I C L E I N F O A B S T R A C T Received: 28 June 2019 The current ongoing scientific debate deals with accumulation of hydronium Revised: 07 August 2019 ions (H3O+) on water surface. Elevated interfacial concentration measured by Accepted: 31 August 2019 using Raman spectroscopy. A strong surface affinity of H3O+ indicated by Raman Available online: 03 September 2019 spectroscopy under similar conditions. Ion adsorption phenomena, H3O+ formation and its structural activity emphasized in our study. Asymmetric water ion adsorption clearly observed in our research. K E Y W O R D S Raman spectroscopy Hydronium Water Infrared spectroscopy G R A P H I C A L A B S T R A C T * Corresponding author's E-mail address: [email protected] Proton Transfer Reaction in Water: Hydronium… 256 Introduction employed for recording Raman spectra with 2– 10 s acquisition time. A scanning area of 30 μm × In nature, interfacial charge formation is 30 μm was applied to avoid laser damage to known as a ubiquitous phenomenon. water. Fundamental mechanism of interfacial charge formation related with its identification. Results and discussions Researchers have been attracted for charge formation development of appropriate models. -
The Influence of Sodium Hydroxide Concentration on the Phase, Morphology and Agglomeration of Cobalt Oxide Nanoparticles and Application As Fenton Catalyst
Digest Journal of Nanomaterials and Biostructures Vol.14, No.4, October-December 2019, p. 1131-1137 THE INFLUENCE OF SODIUM HYDROXIDE CONCENTRATION ON THE PHASE, MORPHOLOGY AND AGGLOMERATION OF COBALT OXIDE NANOPARTICLES AND APPLICATION AS FENTON CATALYST E. L. VILJOENa,*, P. M. THABEDEa, M. J. MOLOTOa, K. P. MUBIAYIb, B. W. DIKIZAa aDepartment of Chemistry, Vaal University of Technology Private, Bag X021, Vanderbijlpark 1900, South Africa bSchool of Chemistry, University of the Witwatersrand, 1 Jan Smuts Avenue, Braamfontein Johannesburg 2000, South Africa The concentration of NaOH was varied from 0.2 M to 0.7 M during the preparation of the cobalt oxide/cobalt oxide hydroxide nanoparticles by precipitation and air oxidation. Cubic shaped and less well defined Co3O4 nanoparticles formed at 0.2 M NaOH. An increase in the NaOH concentration increased the number of well-defined cubic shaped nanoparticles. Agglomerated CoO(OH) particles with different shapes formed at the highest NaOH concentration. The cubic shaped Co3O4 nanoparticles were subsequently used as catalyst for the Fenton degradation of methylene blue and it was found that the least agglomerated nanoparticles were the most catalytically active. (Received June 25, 2019; Accepted December 6, 2019) Keywords: Cobalt oxide, Nanoparticles, Precipitation, pH, Fenton reaction 1. Introduction Controlling the size and the shape of nanoparticles using simple, inexpensive precipitation methods without sophisticated capping molecules, remains a challenge. Literature has indicated that the concentration of the base (pH) is an important parameter to control the size, shape and phase of metal oxide nanoparticles. Obodo et al.[1] used chemical bath deposition at atmospheric pressure and 70 °C to precipitate Co3O4 crystallites on a glass substrate and they showed that the crystallite sizes were larger at a higher pH of 12 in comparison to when a pH of 10 was used. -
SODIUM HYDROXIDE @Lye, Limewater, Lyewater@
Oregon Department of Human Services Office of Environmental Public Health (503) 731-4030 Emergency 800 NE Oregon Street #604 (971) 673-0405 Portland, OR 97232-2162 (971) 673-0457 FAX (971) 673-0372 TTY-Nonvoice TECHNICAL BULLETIN HEALTH EFFECTS INFORMATION Prepared by: ENVIRONMENTAL TOXICOLOGY SECTION OCTOBER, 1998 SODIUM HYDROXIDE @Lye, limewater, lyewater@ For More Information Contact: Environmental Toxicology Section (971) 673-0440 Drinking Water Section (971) 673-0405 Technical Bulletin - Health Effects Information Sodium Hydroxide Page 2 SYNONYMS: Caustic soda, sodium hydrate, soda lye, lye, natrium hydroxide CHEMICAL AND PHYSICAL PROPERTIES: - Molecular Formula: NaOH - White solid, crystals or powder, will draw moisture from the air and become damp on exposure - Odorless, flat, sweetish flavor - Pure solid material or concentrated solutions are extremely caustic, immediately injurious to skin, eyes and respiratory system WHERE DOES IT COME FROM? Sodium hydroxide is extracted from seawater or other brines by industrial processes. WHAT ARE THE PRINCIPLE USES OF SODIUM HYDROXIDE? Sodium hydroxide is an ingredient of many household products used for cleaning and disinfecting, in many cosmetic products such as mouth washes, tooth paste and lotions, and in food and beverage production for adjustment of pH and as a stabilizer. In its concentrated form (lye) it is used as a household drain cleaner because of its ability to dissolve organic solids. It is also used in many industries including glassmaking, paper manufacturing and mining. It is used widely in medications, for regulation of acidity. Sodium hydroxide may be used to counteract acidity in swimming pool water, or in drinking water. IS SODIUM HYDROXIDE NATURALLY PRESENT IN DRINKING WATER? Yes, because sodium and hydroxide ions are common natural mineral substances, they are present in many natural soils, in groundwater, in plants and in animal tissues. -
A Guide to Acids, Acid Strength, and Concentration
A GUIDE TO ACIDS, ACID STRENGTH, AND CONCENTRATION What’s the difference between acid strength and concentration? And how does pH fit in with these? This graphic explains the basics. CH COOH HCl H2SO4 HNO3 H3PO4 HF 3 H2CO3 HYDROCHLORIC ACID SULFURIC ACID NITRIC ACID PHOSPHORIC ACID HYDROFLUORIC ACID ETHANOIC ACID CARBONIC ACID pKa = –7 pKa = –2 pKa = –2 pKa = 2.12 pKa = 3.45 pKa = 4.76 pKa = 6.37 STRONGER ACIDS WEAKER ACIDS STRONG ACIDS VS. WEAK ACIDS ACIDS, Ka AND pKa CONCENTRATION AND pH + – The H+ ion is transferred to a + A decrease of one on the pH scale represents + [H+] [A–] pH = –log10[H ] a tenfold increase in H+ concentration. HA H + A water molecule, forming H3O Ka = pKa = –log10[Ka] – [HA] – – + + A + + A– + A + A H + H H H H A H + H H H A Ka pK H – + – H a A H A A – + A– A + H A– H A– VERY STRONG ACID >0.1 <1 A– + H A + + + – H H A H A H H H + A – + – H A– A H A A– –3 FAIRLY STRONG ACID 10 –0.1 1–3 – – + A A + H – – + – H + H A A H A A A H H + A A– + H A– H H WEAK ACID 10–5–10–3 3–5 STRONG ACID WEAK ACID VERY WEAK ACID 10–15–10–5 5–15 CONCENTRATED ACID DILUTE ACID + – H Hydrogen ions A Negative ions H A Acid molecules EXTREMELY WEAK ACID <10–15 >15 H+ Hydrogen ions A– Negative ions Acids react with water when they are added to it, The acid dissociation constant, Ka, is a measure of the Concentration is distinct from strength. -
A Study of Hydrogen Exchange in Benzene And
A STUDY OF HYDROGEN EXCHANGE IN BENZENE AND SEVERAL ALKYLBENZENES By REX LYNN ELMORE B~chelor of Arts Austin College Sherman, Texas 1960 Submitted to the faculty of the Graduate School of the Oklahpma State University in partial fulfillment of the requirements for the degree of DOCTOR OF PHILOSOPHY August, 1965 J OKLAHOMA Jjf STATE UNIVERSITY .;.;, i' LIBRARY f DEC 6 1965 j' A STUDY OF HYDROGEN EXCHANGE IN BENZE~ AND ,,:.-· ;" . ·..... : SEVERAL ALKYLBENZENES f ~~~~~~~"'~"''""i;·~l'J!'~~ Thesis Approved: 593417 ii .ACKNOWLEDGMENTS Grateful acknowledgment is made to-Dr. E. M. Hodnett, research adviser, for his patience, guidance, and assistance throughout this work; to Dr. O. C. Dermer, head of the Chemistry Department, for his reading of the manuscript prior to its being typed; to Mr. C.R. Williams, formerly in the Chemistry Department, for his assistance in the early phases of the computer programming; to Mr. Preston Gant, Central Research Division of the Continental Oil Company, for helpful suggestions on the tritium assays; and to Mr. Prem S. Juneja for his helpful suggestions concerning experimental details which arose from time to time. Acknowledgment is made of financial assistance in the form of a graduate teaching assistantship in the Chemis.try Department. Also, a research as.sistantship from the Atomic Energy Commission, Contract No. AT(ll-1)-1049, through the Research Foundation is appreciated. Research done during the term of the latter assistantship provided material for this thesis. iii TABLE OF CONTENTS Chapter Page I. INTRODUCTION. 1 II. HISTORICAL, , 3 III. INTRODUCTION TO THE EXPERIMENTAL WORK 14 Objectives and Plan of the Study. -
Properties of Acids and Bases
GREEN CHEMISTRY LABORATORY MANUAL Lab 22 Properties of Acids and Bases TN Standard 4.2: The student will investigate the characteristics of acids and bases. Have you ever brushed your teeth and then drank a glass of orange juice? hat do you taste when you brush your teeth and drink orange juice afterwards. Yuck! It leaves a really bad taste in your mouth, but why? Orange juice and toothpaste by themselves taste good. But the terrible taste W results because an acid/base reaction is going on in your mouth. Orange juice is a weak acid and the toothpaste is a weak base. When they are placed together they neutralize each other and produce a product that is unpleasant to taste. How do you determine what is an acid and what is a base? In this lab we will discover how to distinguish between acids and bases. Introduction Two very important classes of compounds are acids and bases. But what exactly makes them different? There are differences in definition, physical differences, and reaction differences. According to the Arrhenius definition, acids ionize in water to + produce a hydronium ion (H3O ), and bases dissociate in water to produce hydroxide ion (OH -). Physical differences can be detected by the senses, including taste and touch. Acids have a sour or tart taste and can produce a stinging sensation to broken skin. For example, if you have ever tasted a lemon, it can often result in a sour face. Bases have a bitter taste and a slippery feel. Soap and many cleaning products are bases. -
Superacid Chemistry
SUPERACID CHEMISTRY SECOND EDITION George A. Olah G. K. Surya Prakash Arpad Molnar Jean Sommer SUPERACID CHEMISTRY SUPERACID CHEMISTRY SECOND EDITION George A. Olah G. K. Surya Prakash Arpad Molnar Jean Sommer Copyright # 2009 by John Wiley & Sons, Inc. All rights reserved Published by John Wiley & Sons, Inc., Hoboken, New Jersey Published simultaneously in Canada No part of this publication may be reproduced, stored in a retrieval system, or transmitted in any form or by any means, electronic, mechanical, photocopying, recording, scanning, or otherwise, except as permitted under Section 107 or 108 of the 1976 United States Copyright Act, without either the prior written permission of the Publisher, or authorization through payment of the appropriate per-copy fee to the Copyright Clearance Center, Inc., 222 Rosewood Drive, Danvers, MA 01923, (978) 750-8400, fax (978) 750-4470, or on the web at www.copyright.com. Requests to the Publisher for permission should be addressed to the Permissions Department, John Wiley & Sons, Inc., 111 River Street, Hoboken, NJ 07030, (201) 748-6011, fax (201) 748-6008, or online at http://www.wiley.com/go/permission. Limit of Liability/Disclaimer of Warranty: While the publisher and author have used their best efforts in preparing this book, they make no representations or warranties with respect to the accuracy or completeness of the contents of this book and specifically disclaim any implied warranties of merchantability or fitness for a particular purpose. No warranty may be created or extended by sales representatives or written sales materials. The advice and strategies contained herein may not be suitable for your situation. -
Chemistry 20 - Unit 2 - Ph and Poh Notes Name: ______+ - [H3O ] and [OH ]
Chemistry 20 - Unit 2 - pH and pOH Notes Name: _________________________________________ + - [H3O ] and [OH ] + - + - In water both H3O and OH exist H2O + H2O ⇌ H3O + OH + - -14 These concentrations exist in a balanced relationship [H3O ][OH ] = 1.00 x 10 + - This relationship is inversely related ↑ [H3O ] = ↓ [OH ] Example 1: -4 What is the hydroxide ion concentration in a solution with a hydronium ion concentration of 2.59 x 10 M ? + - -14 [H3O ][OH ] = 1.00 x 10 −14 − 1.00×10 [OH ] = + [H3O ] −14 [OH−] = 1.00×10 = 3.86 × 10−11 2.59×10−4 Example 2: If 2.50 g of NaOH was dissolved in water to produce 500mL of solution, what would be the concentration of hydronium and hydroxide ions in solution? + - NaOH ⟶ Na + OH − mol 1 mol 1 [OH ] L = 2.50 g × 40 g × 0.500 L = 0.125 M + - -14 [H3O ][OH ] = 1.00 x 10 −14 −14 [H O+] = 1.00×10 = 1.00×10 = 8.0 × 10−14M 3 [OH−] 1.25 pH Review + pH = − log[H3O ] + −pH [H3O ] = 10 Example 3: What is the pH of a solution of 0.159 M HCl? + - HCl ⟶ H + Cl + pH = − log[H3O ] pH = − log[0.159 M] pH = 0.799 Example 4: What is the hydronium and hydroxide ion concentration of a solution with a pH of 2.42? + −pH −2.42 [H3O ] = 10 = 10 = 0.0038 M + - -14 [H3O ][OH ] = 1.00 x 10 −14 −14 − 1.00×10 1.00×10 −12 [OH ] = + = = 2.63 × 10 M [H3O ] 0.0038 M pOH - Power of OH Since: + - -14 [H3O ][OH ] = 1.00 x 10 Can take the “log” of both sides… pOH = − log[OH−] + - -14 -log([H3O ][OH ]) = -log(1.00 x 10 ) − −pOH [OH ] = 10 + - + - And -log([H3O ][OH ]) = -log[H3O ] + -log[OH ] Therefore… pH + pOH = 14 Example 5: A solution has a pH of 5.750.