Animal Evolution, Bioturbation, and the Sulfate Concentration of the Oceans

Total Page:16

File Type:pdf, Size:1020Kb

Animal Evolution, Bioturbation, and the Sulfate Concentration of the Oceans Animal evolution, bioturbation, and the sulfate SEE COMMENTARY concentration of the oceans Donald E. Canfielda,1 and James Farquhara,b aNordic Center for Earth Evolution, and Institute of Biology, University of Southern Denmark, Campusvej 55, 5230 Odense M, Denmark; and bEarth System Science Interdisciplinary Center and Department of Geology, University of Maryland, College Park, MD 20742 Contributed by Donald E. Canfield, March 3, 2009 (sent for review December 17, 2008) As recognized already by Charles Darwin, animals are geobiologi- 60 cal agents. Darwin observed that worms aerate and mix soils on a 40 massive scale, aiding in the decomposition of soil organic matter. 20 δ34S 0 A similar statement can be made about marine benthic animals. -20 This mixing, also known as bioturbation, not only aides in the -40 decomposition of sedimentary organic material, but as contended 1.5 here, it has also significantly influenced the chemistry of seawater. In particular, it is proposed that sediment mixing by bioturbating f-ratio 1.0 organisms resulted in a severalfold increase in seawater sulfate 0.5 concentration. For this reason, the evolution of bioturbation is linked to the significant deposition of sulfate evaporate minerals, 0 which is largely a phenomena of the Phanerozoic, the last 542 Sulfate 10 million years and the time over which animals rose to prominence. (mM) 1.0 Phanerozoic ͉ evaporite ͉ gypsum ͉ sulfate reduction 0.1 EVOLUTION ith a current concentration of 28 mM, sulfate is the second 0 0.5 1.0 1.5 2.0 2.5 3.0 3.5 4.0 Time (Ga) Wmost abundant anion in seawater. Sulfate enters the ocean mostly from river runoff, with minor contributions from volca- Fig. 1. Graph showing key aspects of the history of the sulfur cycle. (Top) nism (1). It leaves the ocean as either pyrite (FeS2) buried in Isotopic composition of sedimentary sulfides (diamonds) and sulfate (indi- sediments, formed as a product of microbial sulfate reduction, or cated by the 2 red parallel lines) through time. A complete list of data can be as sulfate minerals, mostly gypsum (CaSO ⅐5H O), in evaporite found in the Dataset S1.(Middle) The proportion of total sulfur buried as 4 2 pyrite through time. This is calculated using Eq. 1, using data from the isotope deposits (2). Gypsum precipitates before halite (NaCl) and record. Through the Phanerozoic, the data has been binned from individual GEOLOGY becomes an important evaporite component when the ion Periods, and in the Precambrian, the data were binned in the time intervals: 2ϩ 2- product (IPCaSO4) between Ca and SO4 in unevaporated 542–580 Ma, 580–636 Ma, 636–660 Ma, 660–700 Ma, 750–805 Ma, 805 to 2 2. seawater exceeds 23 mM (3); presently IPCaSO4 is 280 mM The 1000 Ma, and into 300 Ma bins hereafter. Note that between 636 and 700 Ma concentration of Ca2ϩ has varied between 10 and 40 mM over the (between the Sturtian and Marinoan glaciations) the f ratios are off scale (2.9 last 550 million years (4), and if this range applies through Earth and 9.3 in the 2 time bins in this interval) for reasons that are not well 2 2- understood (1). (Bottom) A diagram representing our best estimate for the history, IPCaSO4 would exceed 23 mM with relatively low SO4 levels of 0.5 to 2 mM. If sulfate concentrations fall below this history of seawater sulfate concentrations. See text for details. The vertical Ͻ 2 dotted line at 2.4 Ga represents the ‘‘Great Oxidation Event’’ (15) and the level or if IPCaSO4 becomes 23 mM , the chances for gypsum initial rise in the concentration of atmospheric oxygen (see text for details). supersaturation during evaporation of seawater is reduced. The The line at 0.542 Ga represents the Cambrian–Precambrian boundary. total amount of gypsum deposition from any given parcel of seawater is also limited by sulfate concentration. Previous studies have documented little evidence for gypsum We have used this approach to illustrate to a first order (Fig. 1), 34 deposition before the Mesoproterozoic (1.6 to 1.0 billion years the long term history of gypsum deposition, assuming that ␦ Sin ago) suggesting reduced seawater sulfate concentrations before has been a constant 5 per mil, the most likely value for the recent this time (5). This analysis is predicated on the assumption that Phanerozoic (7). We point out that this value may have varied observations of gypsum abundance faithfully represent the orig- through time (1, 8), but note that within the range of reasonable inal magnitude of gypsum deposition. However, it is known that values (Ϸ4toϷ12 ‰), our conclusions are not changed. gypsum is easily dissolved during weathering (6), and alternative The record of fsulfide (Fig. 1) straddles a value of 1 through all approaches have been developed to evaluate the history of of the Precambrian, implying that gypsum deposition was not a gypsum deposition. One of these derives the history of gypsum major sulfur removal pathway from the oceans until the Pha- deposition from the isotope record of sulfate and sulfide (Fig. 1) nerozoic (last 542 million years) (see also ref 1). This, in turn, (1), with the fraction of the total sulfur leaving the oceans as would imply that sulfate concentrations remained too low to pyrite given by the equation: promote substantial gypsum deposition throughout most of the Precambrian, consistent with independent evidence for the ͓␦34S Ϫ ␦34S ͔ ϭ in sulfate fsulfide ͓␦34 Ϫ ␦34 ͔ [1] Ssulfide Ssulfate Author contributions: D.E.C. designed research; D.E.C. and J.F. performed research; D.E.C. 34 In this equation, ␦ Sx represents either the isotopic composition and J.F. analyzed data; and D.E.C. and J.F. wrote the paper. of sulfur input to the oceans (in), or output from the oceans as The authors declare no conflict of interest. sulfate minerals (sulfate) or sulfide minerals (sulfide), and fsulfide See Commentary on page 8081. is the fraction of the total sulfur removed from the oceans as 1To whom correspondence should be addressed. E-mail: [email protected]. sulfide. The sulfur not deposited as sulfide precipitates as This article contains supporting information online at www.pnas.org/cgi/content/full/ gypsum, so fsulfide Ͻ 1 provides evidence for gypsum deposition. 0902037106/DCSupplemental. www.pnas.org͞cgi͞doi͞10.1073͞pnas.0902037106 PNAS ͉ May 19, 2009 ͉ vol. 106 ͉ no. 20 ͉ 8123–8127 Downloaded by guest on September 29, 2021 history of seawater sulfate concentrations. The keys points in this bines Fe sulfides formed deeper in the sediment with oxidized history include evidence for very low sulfate concentrations of species near the surface, promoting the oxidation of the sulfide. 200 ␮M or less before 2.4 billion years ago (Ga) (9). After this, The global value of x is Ϸ0.033, which is calculated by combining concentrations rose to values probably not exceeding 1 to 2 mM present-day sulfate reduction rate estimates (40 ϫ 1012 over the next 1.6 billion years or so (1, 10–13). The increase at mol⅐yearϪ1) (25) with the burial rate of pyrite (1.2 ϫ 1012 2.4 Ga is coincident with an increase in atmospheric oxygen mol⅐yearϪ1) (26). levels (14–17) promoting the efficient oxidative weathering of In the Precambrian, values for x would have been higher. sulfide minerals on land and increasing the sulfate input to the Geochemical analysis of hundreds of Neoproterozoic sedimen- oceans (18). The first evidence for elevated sulfate concentra- tary rocks shows that these rocks typically contain iron minerals tions (Ϸ16 mM) comes from fluid inclusions in halite deposits such as iron oxides and iron carbonates that are highly reactive collected from the latest Precambrian and earliest Cambrian Ara toward sulfide (27). Because these minerals are in excess, they Group in Oman (19). Other fluid inclusion studies support would have reacted with all sulfide produced by sulfate reduc- seawater sulfate concentrations of 5 to 28 mM through the tion, minimizing sulfide loss from the sediment. Some sulfide Phanerozoic (4). This history is presented in Fig. 1. oxidation may have been promoted by wave and tide-induced Whereas the increase in sulfate concentrations at 2.4 Ga sediment mixing in near shore regions, but except for perhaps in represented the efficient oxidative weathering of sulfides in the latest Neoproterozoic (28), there was no sediment distur- response to increased atmospheric oxygen (e.g., refs. 18 and 20), bance by animals, and mechanisms for reoxidation of sulfide that it is unclear what factor or factors caused the further Phanero- would reduce x to present-day values were lacking. zoic increase in sulfate concentrations. It has been suggested that Sulfate concentration influences both the metabolic activity of the reoxidation of sulfides formed in marine sediments has an sulfate reducers (23) and the depth of sulfate penetration into important influence on seawater sulfate concentrations (21). sediments, which controls the availability of sulfate for sulfate This idea is further developed here, where sulfide oxidation by reduction and values for y. In a previous study of the global bioturbating animals is linked to the Phanerozoic increase in carbon and sulfur cycles, sulfate reduction was assumed to seawater sulfate concentrations. respond linearly to sulfate concentration, the equivalent of y ϭ 1inEq.4 (29). In our view, this value for y is too high because Model the reactive carbon available for sulfate reduction is concen- The link between bioturbation and sulfate concentrations is trated at the sediment surface. This means that although dou- developed in the following equations. First, steady state is bling sulfate concentration, for example, will increase the depth assumed, where the flux of sulfur into the oceans is assumed to of sulfate penetration, the amount of ‘‘extra’’ reactive organic equal the flux out (Eq.
Recommended publications
  • The Determination of Sulfate and Sulfide Sulfur in Rocks Or Minerals
    The Determination of Sulfate and Sulfide Sulfur in Rocks or Minerals By ANGELINA C. VLISIDIS CONTRIBUTIONS TO GEOCHEMISTRY GEOLOGICAL SURVEY BULLETIN 1214-D UNITED STATES GOVERNMENT PRINTING OFFICE, WASHINGTON : 1966 UNITED STATES DEPARTMENT OF THE INTERIOR STEWART L. UDALL, Secretary GEOLOGICAL SURVEY William T. Pecora, Director For sale by the Superintendent of Documents, U.S. Government Printing Office Washington, D.C. 20402 - Price 15 cents (paper cover) CONTENTS Page Abstract_____--__-___-_______-__---____,__-_-__-_---_-_______-_- Dl Introduction. ______________________________________________________ 1 Preparations. _________._.-.__-_-.__.._-_---__----.________._.._____ 2 Standard samples____________________________________________ 2 Reagents. _______________.-_-___-____-__-_-__-_-___-_______-_- 2 Procedure._______________________________________________________ 2 Results__ __________-______-_____----__--_--_----_-_-_-___-___--_ 3 References.._ _____________________________________________________ 5 TABLE Page TABLE 1. Results of sulfide and sulfate sulfur analyses in which varying amounts of a sulfate standard were added to sulfide minerals.. _ D4 m 209-517 66 CONTRIBUTIONS TO GEOCHEMISTRY THE DETERMINATION OF SULFATE AND SULFIDE SULFUR IN ROCKS OR MINERALS By ANGELINA C. VLISEDIS , ABSTRACT A method for the determination of sulfate and sulfide sulfur that occur together in rocks or minerals is presented. All the sulfate sulfur is converted to barium sulfate in an inert atmosphere to prevent oxidation of any sulfide sulfur. Cadmium chloride is added to precipitate any sulfide ion that may be liberated. The sulfate sulfur is then measured indirectly by the determination of the barium and is therefore unaffected by any. subsequent oxidation of the sulfide sulfur.
    [Show full text]
  • Sulfur and Tennessee Row Crops
    W 435 SULFUR AND TENNESSEE ROW CROPS Sulfur (S) deficiencies have become more common in recent years. This publication outlines the importance and role of S in higher plants, summarizes recent research, and defines the University of Tennessee’s current S recommendations for row crops. Tyson B. Raper1, Angela T. McClure2, Frank Yin3 and Blake Brown4 1Assistant Professor, Cotton and Small Grains Specialist, Department of Plant Sciences 2Associate Professor, Corn and Soybean Specialist, Department of Plant Sciences 3Associate Professor, Cropping Systems Agronomist, Department of Plant Sciences 4Director, AgResearch and Education Center at Milan INTRODUCTION Sulfur (S) deficiencies have become more common in recent years due to a reduction in S deposition. Research at the University of Tennessee has begun to answer several key questions on crop response to applications of this nutrient. The objective of this publication is to outline the importance of S and the role it plays within higher plants, describe why the deficiencies are becoming more common, summarize recent research and define the University of Tennessee’s current S recommendations for Tennessee row crops. THE ROLE AND IMPORTANCE OF SULFUR IN HIGHER PLANTS Sulfur is an important nutrient in living systems; it is contained within four common amino acids that assist in the synthesis, structure and function of proteins (Brosnan & Brosnan, 2006). In plant nutrition, S is classified as a macronutrient since it is required in quantities much larger than most micronutrients. Within the macronutrient classification, S falls within the secondary nutrient subclassification along with calcium and magnesium. Although S isn’t a primary macronutrient, it is occasionally referred to as the fourth major nutrient (Stewart, 2010), and if contained within a fertilizer, the S percentage is commonly listed as the fourth Figure 1: Most S containing fertilizers have four number in the fertilizer analysis or grade numbers reported in the analysis or grade, with the first (Figure 1).
    [Show full text]
  • Introduction to Chemistry
    Introduction to Chemistry Author: Tracy Poulsen Digital Proofer Supported by CK-12 Foundation CK-12 Foundation is a non-profit organization with a mission to reduce the cost of textbook Introduction to Chem... materials for the K-12 market both in the U.S. and worldwide. Using an open-content, web-based Authored by Tracy Poulsen collaborative model termed the “FlexBook,” CK-12 intends to pioneer the generation and 8.5" x 11.0" (21.59 x 27.94 cm) distribution of high-quality educational content that will serve both as core text as well as provide Black & White on White paper an adaptive environment for learning. 250 pages ISBN-13: 9781478298601 Copyright © 2010, CK-12 Foundation, www.ck12.org ISBN-10: 147829860X Except as otherwise noted, all CK-12 Content (including CK-12 Curriculum Material) is made Please carefully review your Digital Proof download for formatting, available to Users in accordance with the Creative Commons Attribution/Non-Commercial/Share grammar, and design issues that may need to be corrected. Alike 3.0 Unported (CC-by-NC-SA) License (http://creativecommons.org/licenses/by-nc- sa/3.0/), as amended and updated by Creative Commons from time to time (the “CC License”), We recommend that you review your book three times, with each time focusing on a different aspect. which is incorporated herein by this reference. Specific details can be found at http://about.ck12.org/terms. Check the format, including headers, footers, page 1 numbers, spacing, table of contents, and index. 2 Review any images or graphics and captions if applicable.
    [Show full text]
  • A Novel Exchange Method to Access Sulfated Molecules Jaber A
    www.nature.com/scientificreports OPEN A novel exchange method to access sulfated molecules Jaber A. Alshehri, Anna Mary Benedetti & Alan M. Jones* Organosulfates and sulfamates are important classes of bioactive molecules but due to their polar nature, they are both difcult to prepare and purify. We report an operationally simple, double ion- exchange method to access organosulfates and sulfamates. Inspired by the novel sulfating reagent, TriButylSulfoAmmonium Betaine (TBSAB), we developed a 3-step procedure using tributylamine as the novel solubilising partner coupled to commercially available sulfating agents. Hence, in response to an increasing demand for complementary methods to synthesise organosulfates, we developed an alternative sulfation route based on an inexpensive, molecularly efcient and solubilising cation exchanging method using of-the-shelf reagents. The disclosed method is amenable to a range of diferentially substituted benzyl alcohols, benzylamines and aniline and can also be performed at low temperature for sensitive substrates in good to excellent isolated yield. Organosulfates and sulfamates contain polar functional groups that are important for the study of molecu- lar interactions in the life sciences, such as: neurodegeneration1; plant biology2; neural stem cells3; heparan binding4; and viral infection5. Recent total syntheses including 11-saxitoxinethanoic acid6, various saccharide assemblies7–10, and seminolipid11 have all relied on the incorporation of a highly polar organosulfate motif. Importantly, the frst in class organosulfate containing antibiotic, Avibactam12, has led to the discovery of other novel β-lactamase inhibitors 13,14. Despite the importance of the sulfate group, there remain difculties with the ease of their synthesis to enable further biological study. Our own interest in developing sulfated molecules resulted from a medicinal chemistry challenge to reliably synthesise sulfated glycomimetics 15–18.
    [Show full text]
  • Sulfur Dioxide in Workplace Atmospheres (Bubbler)
    Withdrawn Provided For Historical Reference Only SULFUR DIOXIDE IN WORKPLACE ATMOSPHERES (BUBBLER) ♦ Method Number: ID-104 Matrix: Air OSHA PEL Sulfur Dioxide (Final Rule Limit): 2 ppm (Time Weighted Limit) 5 ppm (Short-Term Exposure Limit) Sulfur Dioxide (Transitional Limit): 5 ppm (Time Weighted Limit) Collection Device: A calibrated personal sampling pump is used to draw a known volume of air through a midget-fritted glass bubbler containing 10 to 15 mL of 0.3 N hydrogen peroxide. Recommended Air Volume: 15 to 60 L Recommended Sampling Rate: 1 L/min Analytical Procedure: Samples are directly analyzed with no sample preparation by ion chromatography as total sulfate. Detection Limit Qualitative: 0.0041 ppm (60-L air volume) Quantitative: 0.010 ppm (60-L air volume) Precision and Accuracy Validation Level: 2.5 to 10.0 ppm (60-L air volume) CVT 0.012 Bias -0.046 Overall Error ±7% Method Classification: Validated Method Chemist: Ted Wilczek, Edward Zimowski Date (Date Revised): 1981 (December, 1989) Commercial manufacturers and products mentioned in this method are for descriptive use only and do not constitute endorsements by USDOL-OSHA. Similar products from other sources can be substituted. Branch of Inorganic Methods Development OSHA Technical Center Salt Lake City, Utah 1 of 9 Note: OSHA no longer uses or supports this method (November 2019). Withdrawn Provided For Historical Reference Only 1. Introduction This method describes the collection and analysis of airborne sulfur dioxide (SO2) using midget-fritted glass bubblers (MFGBs) in the workplace. It is applicable for both short-term (STEL) and time weighted average (TWA) exposure evaluations.
    [Show full text]
  • Sulfate in Well Water 08/02/2019R Environmental Health Division
    Sulfate Health Risks for Animals . Anion exchange is the most common method of removing large quantities of Sulfate occurs naturally in most of Minnesota’s Animals are also sulfate from water for commercial, groundwater. Higher levels of sulfate are sensitive to high livestock, and public supplies. It is not common in the western part of the state. At levels of sulfate. commonly used for individual household high levels, sulfate can give water a bitter or In young animals, water treatment. It is a process that medicinal taste and can have laxative effects. high levels may replaces negatively charged ions (such as You can find out the level of sulfate in your be associated sulfate) with sodium chloride or potassium water by having the water tested at a with severe, chronic diarrhea and even death. chloride (salts). Animals tend to get used to sulfate over time. laboratory. Adsorptive media filtration has a charged Diluting water high in sulfate with water low in media bed that can force ions of the sulfate can help avoid problems of diarrhea opposite charge (such as sulfate) to be Health Risks for Humans and dehydration in young animals and animals pulled out of the water and attach to the not used to drinking high sulfate water. People who are not media. used to water with high Contact a veterinarian or your county office of sulfate can get diarrhea the Minnesota Extension Service for more Learn more about these treatment options at and dehydration from information. the “Home Water Treatment” webpage. drinking the water. Note that water softeners, carbon filters, and Infants are often more Ways to Treat Sulfate sediment filters do not remove sulfate.
    [Show full text]
  • Sodium Dodecyl Sulphate
    SAFETY DATA SHEET Creation Date 24-Nov-2010 Revision Date 18-Jan-2018 Revision Number 5 1. Identification Product Name SDS Micropellets (sodium dodecyl sulfate) Cat No. : BP8200-100; BP8200-5; BP8200-500; BP8200-10 CAS-No 151-21-3 Synonyms Sodium lauryl sulfate; SDS; Dodecyl Sodium Sulfate Recommended Use Laboratory chemicals. Uses advised against Not for food, drug, pesticide or biocidal product use Details of the supplier of the safety data sheet Company Fisher Scientific One Reagent Lane Fair Lawn, NJ 07410 Tel: (201) 796-7100 Emergency Telephone Number CHEMTRECÒ, Inside the USA: 800-424-9300 CHEMTRECÒ, Outside the USA: 001-703-527-3887 2. Hazard(s) identification Classification This chemical is considered hazardous by the 2012 OSHA Hazard Communication Standard (29 CFR 1910.1200) Acute oral toxicity Category 4 Skin Corrosion/irritation Category 2 Serious Eye Damage/Eye Irritation Category 1 Combustible dust Yes Label Elements Signal Word Danger Hazard Statements May form combustible dust concentrations in air Harmful if swallowed Causes skin irritation Causes serious eye damage ______________________________________________________________________________________________ Page 1 / 7 SDS Micropellets (sodium dodecyl sulfate) Revision Date 18-Jan-2018 ______________________________________________________________________________________________ Precautionary Statements Prevention Wash face, hands and any exposed skin thoroughly after handling Do not eat, drink or smoke when using this product Wear protective gloves/protective clothing/eye protection/face protection Skin IF ON SKIN: Wash with plenty of soap and water If skin irritation occurs: Get medical advice/attention Take off contaminated clothing and wash before reuse Eyes IF IN EYES: Rinse cautiously with water for several minutes. Remove contact lenses, if present and easy to do.
    [Show full text]
  • Sulfate Salts in Gasoline and Ethanol Fuels – Historical Perspective and Analysis of Available Data Robert L
    Sulfate Salts in Gasoline and Ethanol Fuels – Historical Perspective and Analysis of Available Data Robert L. McCormick and Teresa L. Alleman National Renewable Energy Laboratory Janet Yanowitz Ecoengineering, Inc. NREL is a national laboratory of the U.S. Department of Energy Office of Energy Efficiency & Renewable Energy Operated by the Alliance for Sustainable Energy, LLC This report is available at no cost from the National Renewable Energy Laboratory (NREL) at www.nrel.gov/publications. Technical Report NREL/TP-5400-69001 September 2017 Contract No. DE-AC36-08GO28308 Sulfate Salts in Gasoline and Ethanol Fuels – Historical Perspective and Analysis of Available Data Robert L. McCormick and Teresa L. Alleman National Renewable Energy Laboratory Janet Yanowitz Ecoengineering, Inc. Prepared under Task No. VTOP.10335.04.01.03 NREL is a national laboratory of the U.S. Department of Energy Office of Energy Efficiency & Renewable Energy Operated by the Alliance for Sustainable Energy, LLC This report is available at no cost from the National Renewable Energy Laboratory (NREL) at www.nrel.gov/publications. National Renewable Energy Laboratory Technical Report 15013 Denver West Parkway NREL/TP-5400-69001 Golden, CO 80401 September 2017 303-275-3000 • www.nrel.gov Contract No. DE-AC36-08GO28308 NOTICE This report was prepared as an account of work sponsored by an agency of the United States government. Neither the United States government nor any agency thereof, nor any of their employees, makes any warranty, express or implied, or assumes any legal liability or responsibility for the accuracy, completeness, or usefulness of any information, apparatus, product, or process disclosed, or represents that its use would not infringe privately owned rights.
    [Show full text]
  • 5. POTENTIAL for HUMAN EXPOSURE 5.1 OVERVIEW Sulfur
    SULFUR DIOXIDE 111 5. POTENTIAL FOR HUMAN EXPOSURE 5.1 OVERVIEW Sulfur dioxide has been identified in at least 16 of the 1,467 current or former EPA National Priorities List (NPL) hazardous wastes sites (HazDat 1998). However, the number of sites evaluated for sulfur dioxide is not known. The frequency of these sites within the United States can be seen in Figure 5-l. Atmospheric sulfur dioxide is formed as a by-product of the combustion of fuel from power generation and industrial activities, and by the oxidation of reduced gases in the atmosphere. Volcanic activity also contributes to the levels of atmospheric sulfur dioxide. The atmospheric lifetime of sulfur dioxide is about 10 days (IARC 1992). Sulfur dioxide is oxidized rapidly by both homogeneous and heterogeneous reactions and is removed from the atmosphere by precipitation and by dry deposition on surfaces, mainly as sulfuric acid. Inhalation of sulfur dioxide, by the general population residing near industrial sources and by workers exposed to sulfur dioxide, is generally the main route of human exposure to the chemical. It should be noted that the amount of sulfur dioxide detected by chemical analysis is not necessarily the amount that is bioavailable. 5. 2 RELEASES TO THE ENVIRONMENT Releases of sulfur dioxide to the environment from large processing facilities are not required to be reported to the Toxics Release Inventory (TRI). Releases of sulfur dioxide are not required to be reported under SARA Section 3 13. Consequently, there are no data for this compound in the current TRI. Sulfur dioxide has been identified in a variety of environmental media (air, surface water, groundwater, soil, and sediment) collected at 16 of the 1,467 NPL hazardous waste sites (HazDat 1998).
    [Show full text]
  • Stratospheric Dynamical Response and Ozone Feedbacks in The
    Journal of Geophysical Research: Atmospheres RESEARCH ARTICLE Stratospheric Dynamical Response and Ozone Feedbacks 10.1002/2017JD026912 in the Presence of SO2 Injections Special Section: Simulations of Stratospheric Jadwiga H. Richter1 , Simone Tilmes1,2 , Michael J. Mills2 , Joseph J. Tribbia1 , Sulfate Aerosol Geoengineering 3 4,5 2 1 with the Whole Atmosphere Ben Kravitz , Douglas G. MacMartin , Francis Vitt , and Jean-Francois Lamarque Community Climate Model (WACCM) 1Climate and Global Dynamics Laboratory, National Center for Atmospheric Research, Boulder, CO, USA, 2Atmospheric Chemistry, Observations, and Modeling Laboratory, National Center for Atmospheric Research, Boulder, CO, USA, 3Pacific This article is a companion to Northwest National Laboratory, Richland, WA, USA, 4Mechanical and Aerospace Engineering, Cornell University, Ithaca, Kravitz et al. (2017) NY, USA, 5Department of Computing and Mathematical Sciences, California Institute of Technology, Pasadena, CA, USA https://doi.org/10.1002/2017JD026874, MacMartin et al. (2017) https://doi.org/10.1002/2017JD026868, Tilmes et al. (2017) Abstract Injections of sulfur dioxide into the stratosphere are among several proposed methods of solar https://doi.org/10.1002/2017JD026888, radiation management. Such injections could cool the Earth’s climate. However, they would significantly and Mills et al. (2017) alter the dynamics of the stratosphere. We explore here the stratospheric dynamical response to sulfur https://doi.org/10.1002/2017JD027006. dioxide injections ∼5 km above the tropopause at multiple latitudes (equator, 15∘S, 15∘N, 30∘S and 30∘N) using a fully coupled Earth system model, Community Earth System Model, version 1, with the Whole Key Points: Atmosphere Community Climate Model as its atmospheric component (CESM1(WACCM)).
    [Show full text]
  • Cesium Sulfate, Purity Min. 99 % (50 % Solution in Water)
    TECHNICAL DATA SHEET Date of Issue: 2016/08/29 Cesium Sulfate, purity min. 99 % (50 % solution in water) CAS-No. 10294-54-9 EC-No. 233-662-6 REACH No. 01-2119977125-33 Molecular Formula Cs₂SO₄ Product Number 423601 APPLICATION This product is particularly used as promoter in heterogeneous catalysts (e.g. sulfuric acid, phthalic anhydride etc.). PURITY min. 99 % SPECIFICATION Li max. 5 ppm Na max. 200 ppm K max. 500 ppm Rb max. 2000 ppm Ca max. 1000 ppm Mg max. 2500 ppm Sr max. 100 ppm Ba max. 10 ppm Al max. 20 ppm Cl max. 100 ppm Deliveries are accompanied by a lot specific certificate of analysis. If any of these values is critical to your application, please let us know. The information presented herein is believed to be accurate and reliable, but is presented without guarantee or responsibility on the part of Albemarle Corporation and its subsidiaries and affiliates. It is the responsibility of the user to comply with all applicable laws and regulations and to provide for a safe workplace. The user should consider any health or safety hazards or information contained herein only as a guide, and should take those precautions which are necessary or prudent to instruct employees and to develop work practice procedures in order to promote a safe work environment. Further, nothing contained herein shall be taken as an inducement or recommendation to manufacture or use any of the herein materials or processes in violation of existing or future patent. Technical data sheets may change frequently. You can download the latest version from our website www.albemarle-lithium.com.
    [Show full text]
  • MAGNESIUM SULFATE Chemical and Technical Assessment
    MAGNESIUM SULFATE Chemical and Technical Assessment Revised by Madduri V. Rao, Ph.D. for the 68th JECFA (Original prepared by Yoko Kawamura, Ph.D. for the 63rd JECFA) 1. Summary Magnesium sulfate was evaluated by the Committee at its 63rd meeting. The outstanding information on functional uses other than nutrient supplement as well as information on commercial use of anhydrous magnesium sulfate and magnesium sulfate was requested for evaluation by the 68th JECFA meeting. Magnesium sulfate is commercially available as heptahydrate, monohydrate, anhydrous or dried form containing the equivalent of 2 - 3 waters of hydration. Magnesium sulfate occurs naturally in seawater, mineral springs and in minerals such as kieserite and epsomite. Magnesium sulfate heptahydrate is manufactured by dissolution of kieserite in water and subsequent crystallization of the heptahydrate. Magnesium sulfate is also prepared by sulfation of magnesium oxide. It is produced with one or seven molecules of water of hydration or in a dried form containing the equivalent of about 2 - 3 waters of hydration. Magnesium sulfate is available as brilliant colourless crystals, granular crystalline powder or white powder with a bitter salty cooling taste. Crystals effloresce in warm, dry air. It is freely soluble in water, very soluble in boiling water, and sparingly soluble in alcohol. Magnesium sulfate is used as a nutrient, firming agent and flavour enhancer. It is also used as a fermentation aid in the processing of beer and malt beverages. No food uses have been identified for the anhydrous form of magnesium sulfate. 2. Description Magnesium sulfate occurs with one (monohydrate), seven (heptahydrate), or no (anhydrous) molecules of water of hydration.
    [Show full text]