7 Natural Abundance of Radioactive Isotopes

Total Page:16

File Type:pdf, Size:1020Kb

7 Natural Abundance of Radioactive Isotopes 8 NATURAL ABUNDANCE OF RADIOACTIVE ISOTOPES OF C AND H In this chapter the two nuclides, 14C and 3H, will be treated that are the most relevant in the hydrological cycle. Chapter 12 contains a survey of the isotopes with less extensive applications. 8.1 THE RADIOACTIVE CARBON ISOTOPE 8.1.1 ORIGIN OF 14C, DECAY AND HALF-LIFE The natural occurrence of the radioactive carbon isotope, 14C or radiocarbon, was first recognised by W.F. Libby (1946). It is naturally formed in the transitional region between the stratosphere and troposphere about 12 km above the earth's surface through the nuclear reaction: 14N + n J 14C + p (8.1) The thermal neutrons required are produced by reactions between very high-energy primary cosmic ray protons and molecules of the atmosphere. 14C thus formed very soon oxidises to 14 14 CO, and ultimately to CO2 which mixes with the inactive atmospheric CO2 (Fig.8.1). 14 Through exchange with oceanic dissolved carbon (primarily bicarbonate), most CO2 molecules enter the oceans and living marine organisms. Some are also assimilated by land plants, so that all living organisms, vegetable as well as animal, contain 14C in concentrations about equal (Sect.8.1.3) to that of atmospheric CO2. 14C decays according to: 14C J 14N + ß (8.2) with a maximum ß energy of 156 keV and a half-life of 5730 ± 40 years (Godwin, 1962) (Fig.8.2). Originally the half-life was thought to be 5568 years, so that during the first decade or two 14C age determinations were based on the "wrong" half-life. Later, when the "better" half-life became known, so many 14C ages were already published that, in order to avoid confusion, it was decided that the original half-life should continued to be used for reporting 14C ages. Moreover, it was meanwhile known that ages would still be in error, even using the 14 right half-life, because of the natural variations in the C content of atmospheric CO2 during geologic times and deviating from the present. These errors were even larger. Nowadays the 125 Chapter 8 cosmic radiation 14 14 14 14 N + n J C + p J C N + 14 14 C C 14 C 14 12 CO2 + CO2 12 CO2 exchange assimilation fossil nuclear bomb fuel exchange 14 H CO3 14 shells humus CO2 14 LAKE Ca CO3 OCEAN groundwater table ageing 12 14 12 + Ca CO3 + H2O J H CO3 + H CO3 Fig.8.1 Origin and distribution of 14C in nature. The natural 14C concentration by the production by neutrons from cosmic radiation has been influenced by -chronologically- the addition 14 14 to the air of CO2 without C by the combustion of fossil fuels and the production of C by neutrons released by the fission and fusion reactions during nuclear explosions. 14C calibration, based on the known 14C content of tree rings with exactly known age, removes both errors at once (Sect.8.1.4). The production and distribution of 14C in nature occurs through series of chemical and biological processes which has become stationnary throughout much of geologic time. As a consequence, the concentration of 14C in the atmosphere, oceans and biosphere reached a steady-state value which has been almost constant during a geologic period which is long compared to the life span of a 14C nucleus. This natural concentration, 14C/C, is of the order of 10-12, which is equivalent to a specific activity of about 0.25 Bq/gC (disintegrations per second per gram of carbon) (Sect.5.3). 8.1.2 REPORTING 14C VARIATIONS AND THE 14C STANDARD Three modes of reporting 14C activities are in use, in part analogous to the conventions internationally agreed (IAEA) for stable isotopes (Stuiver and Polach, 1977; Mook and Van der Plicht, 1999). 126 Radioactive Isotopes of Hydrogen and Carbon 14 C T1/2 = 5730 a 3 H T1/2 = 12.43 a Emax = 156 keV Emax = 18 keV 3He 14N 3 14 Anatural = 0.6 Bq / liter H2O Anatural = 250 Bq / kg C Fig.8.2 Decay schemes of tritium and radiocarbon. Both nuclides are pure emitters. The present-day specific activities are given as 3A and 14A. The absolute (specific) 14C activity, that is the 14C radioactivity (in Bq or, conventionally, in disintegrations per minute (dpm) per gram of carbon) is given the symbol 14A = number of disintegrations per minute (dpm/gC) (8.3) It is extremely difficult to make an absolute measurement of a 14C activity. Moreover, the absolute 14C content of a sample is generally not relevant. Therefore, the sample activities are compared with the activity of a standard. In reality, the number of 14C registrations ( registrations from 14C decay in radiometric detectors such as proportional counters and liquid scintillation counters, registrations of 14C concentration in AMS systems) are related to the number of registrations from the standard under equal conditions. This results in a 14C activity ratio or 14C concentration ratio: 14 14 14 Asample A a 14 14 A reference A R 14 Cdecayrate in thesample 14 Cconcentration in thesample (8.4) 14 Cdecayrate in the reference 14 Cconcentration in the reference Because in the nominator and denominator of the last two fractions the detection efficiencies are cancelled being equal for sample and reference material, the use of the ratio 14a is adequate for any type of measuring technique. 127 Chapter 8 Henceforth, the symbol 14A may be used for the 14C content (radioactivity or concentration) of a sample, whether the analytical technique applied is radiometric or mass spectrometric (AMS). Under natural circumstances the values of 14a are between 0 and 1. In order to avoid the use of decimals, it is general practice to report these values in %, which is equivalent to the factor 10 2 (see also Sect.11.5.1). It is incorrect to write 14a/102 instead of merely 14a. In several cases the differences in 14C content between the project samples are small. Therefore, the use has been taken over from the stable-isotope field to define relative abundances, in casu the relative 14C content (activity or concentration), 14, defined as the difference between sample and reference 14C content as a fraction of the reference value: 14 A 14A 14 A 14 R 1 14a 1 (P102 %) (8.5) 14 14 A R A R The values of are small numbers and therefore generally given in ‰, which is equivalent to the factor 10 3 (cf. Sect.4.1). In Chapter 7 we have seen that during any process in nature isotope fractionation occurs, not only for the stable isotopes but similarly for the radioactive isotope such as 14C. Neglecting this effect would introduce an error in an age determination, because the original 14C content of the material would be different from what we assume. The degree of fractionation is nicely 13 indicated by the value of the material. An example is the apparent difference in age 13 13 between C3 plants such as trees ( W 25‰) and a C4 plant such as sugar cane ( W 10‰), each assimilating the same atmospheric CO2. Therefore, in defining the standard activity, but also in our treatment of all 14C data, we have to normalise the 14C results to the same 13 value. In Chapter 11 we will go into more detail. Here we suffice by stating that by international agreement all 14C results have to be corrected for a deviation of the 13 value from 25‰, with the exception of Ox1 which has to be corrected to 19‰. The 14C standard activity or concentration was chosen to represent as closely as possible the 14C content of carbon in naturally growing plants. The 14C standard activity does not need to be, in fact it is not, equal to the 14C activity of the standard. The definition of the standard 14C activity is based on 95% of the specific activity of the original NBS oxalic acid (Ox1) in the year AD1950 (Karlén et al., 1966), as will be discussed in more detail later. The 14C standard activity is defined by: 14 0 14 0 M M As tan dard 0.95 AOx1 13.56 0.07 dpm / gC 0.226 0.001 Bq / gC (8.6) 128 Radioactive Isotopes of Hydrogen and Carbon dpm/gC means disintegrations per minute per gram of carbon, while the superscript 0 refers to the fact that the definition is valid for the year 1950 only. Because the original supply of oxalic acid has been exhausted, a new batch of oxalic acid (Ox2) is available for distribution by the NIST (formerly US-Nat. Bureau of Standards). Through careful measurement by a number of laboratories (Mann, 1983), the 14C activity has become related to that of the original Ox1 by: 14 0 M 14 0 AOx2 (1.2736 0.0004) AOx1 (8.7) Both activities refer to AD1950. Consequently the standard activity is: 14 0 14 0 As tan dard 0.7459 AOx2 (8.8) where the 14A0 values for Ox1 and Ox2 refer to the activity of the material in 1950, irrespective of the time of measurement. Details on the measurement and calculation procedures are given in Chapter 11. A survey of available 14C reference samples of different compounds and ages is given in Table 11.5. 8.1.3 SURVEY OF NATURAL 14C VARIATIONS 8.1.3.1 ATMOSPHERIC CO2 Certain fluctuations occur in the stationary state mentioned in Sect.8.1.1. Because of variations in cosmic ray intensity, and in climate affecting the size of the carbon reservoirs, the 14C content of atmospheric carbon has not always been precisely the same as at present.
Recommended publications
  • 12 Natural Isotopes of Elements Other Than H, C, O
    12 NATURAL ISOTOPES OF ELEMENTS OTHER THAN H, C, O In this chapter we are dealing with the less common applications of natural isotopes. Our discussions will be restricted to their origin and isotopic abundances and the main characteristics. Only brief indications are given about possible applications. More details are presented in the other volumes of this series. A few isotopes are mentioned only briefly, as they are of little relevance to water studies. Based on their half-life, the isotopes concerned can be subdivided: 1) stable isotopes of some elements (He, Li, B, N, S, Cl), of which the abundance variations point to certain geochemical and hydrogeological processes, and which can be applied as tracers in the hydrological systems, 2) radioactive isotopes with half-lives exceeding the age of the universe (232Th, 235U, 238U), 3) radioactive isotopes with shorter half-lives, mainly daughter nuclides of the previous catagory of isotopes, 4) radioactive isotopes with shorter half-lives that are of cosmogenic origin, i.e. that are being produced in the atmosphere by interactions of cosmic radiation particles with atmospheric molecules (7Be, 10Be, 26Al, 32Si, 36Cl, 36Ar, 39Ar, 81Kr, 85Kr, 129I) (Lal and Peters, 1967). The isotopes can also be distinguished by their chemical characteristics: 1) the isotopes of noble gases (He, Ar, Kr) play an important role, because of their solubility in water and because of their chemically inert and thus conservative character. Table 12.1 gives the solubility values in water (data from Benson and Krause, 1976); the table also contains the atmospheric concentrations (Andrews, 1992: error in his Eq.4, where Ti/(T1) should read (Ti/T)1); 2) another category consists of the isotopes of elements that are only slightly soluble and have very low concentrations in water under moderate conditions (Be, Al).
    [Show full text]
  • 1 Introduction
    1 Introduction WHO commissions reviews and undertakes health risk assessments associated with exposure to potentially hazardous physical, chemical and biological agents in the home, work place and environment. This monograph on the chemical and radiological hazards associated with exposure to depleted uranium is one such assessment. The purpose of this monograph is to provide generic information on any risks to health from depleted uranium from all avenues of exposure to the body and from any activity where human exposure could likely occur. Such activities include those involved with fabrication and use of DU products in industrial, commercial and military settings. While this monograph is primarily on DU, reference is also made to the health effects and behaviour of uranium, since uranium acts on body organs and tissues in the same way as DU and the results and conclusions from uranium studies are considered to be broadly applicable to DU. However, in the case of effects due to ionizing radiation, DU is less radioactive than uranium. This review is structured as broadly indicated in Figure 1.1, with individual chapters focussing on the identification of environmental and man-made sources of uranium and DU, exposure pathways and scenarios, likely chemical and radiological hazards and where data is available commenting on exposure-response relationships. HAZARD IDENTIFICATION PROPERTIES PHYSICAL CHEMICAL BIOLOGICAL DOSE RESPONSE RISK EVALUATION CHARACTERISATION BACKGROUND EXPOSURE LEVELS EXPOSURE ASSESSMENT Figure 1.1 Schematic diagram, depicting areas covered by this monograph. It is expected that the monograph could be used as a reference for health risk assessments in any application where DU is used and human exposure or contact could result.
    [Show full text]
  • Sources of Variation in the Stable Isotopic Composition of Plants*
    CHAPTER 2 Sources of variation in the stable isotopic composition of plants* JOHN D. MARSHALL, J. RENÉE BROOKS, AND KATE LAJTHA Introduction The use of stable isotopes of carbon, nitrogen, oxygen, and hydrogen to study physiological processes has increased exponentially in the past three decades. When Harmon Craig (1953, 1954), a geochemist and early pioneer of natural abundance stable isotopes, fi rst measured isotopic values of plant materials, he found that plants tended to have a fairly narrow δ13C range of −25 to −35‰. In these initial surveys, he was unable to fi nd large taxonomic or environmental effects on these values. Since that time ecologists have identi- fi ed clear isotopic signatures based not only on different photosynthetic pathways, but also on ecophysiological differences, such as photosynthetic water-use effi ciency (WUE) and sources of water and nitrogen used. As large empirical databases have accumulated and our theoretical understanding of isotopic composition has improved, scientists have continued to discover mismatches between theoretical and observed values, as well as confounding effects from sources and factors not previously considered. In the best tradi- tion of science, these discoveries have led to important new insights into physiological or ecological processes, as well as new uses of stable isotopes in plant ecophysiology. This chapter reviews the most common applications of stable isotope analysis in plant ecophysiology. Carbon isotopes Photosynthetic pathways 13 Plants contain less C than the atmospheric CO2 on which they rely for photosynthesis. They are therefore “depleted” of 13C relative to the atmo- sphere. This depletion is caused by enzymatic and physical processes that discriminate against 13C in favor of 12C.
    [Show full text]
  • Characterisation of Various Types of Alloy by K0-Neutron Activation Analysis
    A27 CHARACTERISATION OF VARIOUS TYPES OF ALLOY BY K0-NEUTRON ACTIVATION ANALYSIS M. WASIM, N. KHALID, M. ARIF Chemistry Division, Pakistan Institute of Nuclear Science and Technology, Islamabad, Pakistan N.A. LODHI Isotope Production Division, Pakistan Institute of Nuclear Science and Technology, Islamabad, Pakistan Abstract Samples of certified alloys were analysed by semi-absolute, standardless k0-instrumental neutron activation analysis (k0-INAA) for compositional decoding. Irradiations were performed at Miniaturised Neutron Source Reactor (MNSR) located at Pakistan Institute of Nuclear Science and Technology, Islamabad having nominal thermal neutron fluxes of 1×1012 cm-2s-1. The experimentally optimised parameters for NAA suggested a maximum of three irradiations for the quantification of 21 elements within 5 days. The same experimental conditions produced quantitative results of 13 elements, which were not reported by the supplier of the reference materials. All reference concentrations were within 95% confidence interval of the determined concentrations. 1. INTRODUCTION Worldwide interest in the determination of elements in different materials has led to the development of many analytical techniques. The commonly used techniques include inductively coupled plasma with optical emission spectrometry (ICP-OES), X-ray fluorescence spectrometry (XRF), atomic absorption spectrometry (AAS) [1], arc/spark optical emission spectrometry, ICP with mass spectrometry and laser-induced breakdown spectroscopy [2-4]. Nuclear analytical techniques also play important role in material characterisation [5]. Among these the noticeable are particle induced X-ray emission, proton activation analysis [6,7], prompt gamma-ray neutron activation [8], fast neutron activation analysis [9,10] and thermal neutron activation analysis (NAA) [11,12]. The non-nuclear techniques apply relative standardisation, also known as classical linear calibration, whereby a calibration curve is drawn by using three or more calibration standards.
    [Show full text]
  • Measuring Long-Range 13C–13C Correlations on a Surface Under
    Ames Laboratory Accepted Manuscripts Ames Laboratory 10-13-2017 Measuring Long-Range 13C–13C Correlations on a Surface under Natural Abundance Using Dynamic Nuclear Polarization-Enhanced Solid- State Nuclear Magnetic Resonance Takeshi Kobayashi Ames Laboratory, [email protected] Igor I. Slowing Iowa State University and Ames Laboratory, [email protected] Marek Pruski Iowa State University and Ames Laboratory, [email protected] Follow this and additional works at: http://lib.dr.iastate.edu/ameslab_manuscripts Part of the Materials Chemistry Commons, and the Physical Chemistry Commons Recommended Citation Kobayashi, Takeshi; Slowing, Igor I.; and Pruski, Marek, "Measuring Long-Range 13C–13C Correlations on a Surface under Natural Abundance Using Dynamic Nuclear Polarization-Enhanced Solid-State Nuclear Magnetic Resonance" (2017). Ames Laboratory Accepted Manuscripts. 33. http://lib.dr.iastate.edu/ameslab_manuscripts/33 This Article is brought to you for free and open access by the Ames Laboratory at Iowa State University Digital Repository. It has been accepted for inclusion in Ames Laboratory Accepted Manuscripts by an authorized administrator of Iowa State University Digital Repository. For more information, please contact [email protected]. Measuring Long-Range 13C–13C Correlations on a Surface under Natural Abundance Using Dynamic Nuclear Polarization-Enhanced Solid-State Nuclear Magnetic Resonance Abstract We report that spatial (<1>nm) proximity between different molecules in solid bulk materials and, for the first time, different moieties on the surface of a catalyst, can be established without isotope enrichment by means of homonuclear CHHC solid-state nuclear magnetic resonance experiment. This 13C–13C correlation measurement, which hitherto was not possible for natural-abundance solids, was enabled by the use of dynamic nuclear polarization.
    [Show full text]
  • Determination of Particulate and Dissolved 228Th in Seawater Using a Delayed Coincidence Counter
    MARCHE-03183; No of Pages 7 Marine Chemistry xxx (2014) xxx–xxx Contents lists available at ScienceDirect Marine Chemistry journal homepage: www.elsevier.com/locate/marchem Determination of particulate and dissolved 228Th in seawater using a delayed coincidence counter Kanchan Maiti a,b,⁎, Matthew A. Charette b, Ken O. Buesseler b,KuanboZhoub, Paul Henderson b, Willard S. Moore c,PaulMorrisb, Lauren Kipp b a Department of Oceanography and Coastal Sciences Louisiana State University, Baton Rouge, LA 70803, USA b Department of Marine Chemistry and Geochemistry Woods Hole Oceanographic Institution, Woods Hole, MA 02543, USA c Department of Earth and Ocean Sciences, University of South Carolina, Columbia, SC 29208, USA article info abstract Article history: The application of thorium-228 towards understanding particle dynamics in the open ocean is limited because of Received 13 August 2014 its low natural abundance in seawater and associated sampling and analytical challenges. Here we describe a fast Received in revised form 26 November 2014 and nondestructive method for measuring both dissolved and particulate 228Th activities in the open ocean using Accepted 7 December 2014 Radium Delayed-Coincidence Counters (RaDeCC). Particulate and dissolved samples were collected from the Available online xxxx upper 1000 m of the Sargasso Sea water column during the US GEOTRACES intercalibration cruise using large vol- ume in situ pumps equipped with Quartz microfiber filters and MnO impregnated cartridges. Samples were di- Keywords: 2 fi Thorium-228 rectly counted on the RaDeCC system using a custom machined lter sample holder and a commercially available Particle flux cartridge holder followed by traditional alpha counting.
    [Show full text]
  • Journal of Analytical Atomic Spectrometry ARTICLE
    CW-127610-CONF-004, Rev 0 UNRESTRICTED Journal of Analytical Atomic Spectrometry ARTICLE Determination of Radiogenic Silicon and its Isotopes in Neutron Irradiated Aluminum Alloys by ICP-MS Received 00th January 20xx, a a a Accepted 00th January 20xx Y. Shi,* C. Broome , and R. Collins DOI: 10.1039/x0xx00000x Aluminum alloy is frequently used as component material in research nuclear reactors. Thermal neutron irradiation of aluminum causes it to undergo transmutation to silicon. The production of silicon inside of aluminum alloy changes its www.rsc.org/ material and mechanical properties. Furthermore, the concentration and the isotopic composition of the radiogenic silicon provides information on the irradiation history of the material and operation history of the reactor both of which are important to nuclear forensics and nuclear archaeology. An analytical method has been developed to determine the concentration and isotopic composition of radiogenic silicon using sector field ICP-MS. Applying a mass resolution of 3000 avoided severe spectral interferences from poly-atomic and doubly charged ion species generated from the solution matrix observed using lower resolution mass spectrometers. The measured content of radiogenic silicon in aluminium alloy materials irradiated with known fluence of thermal neutrons agreed well with the theoretically predicted values. Introduction Historically, many analytical techniques have been applied to determine silicon in aluminum based alloys. The classic With its good formability, ease of welding, and corrosion gravimetric method has been used for a long time and adapted resistance, aluminum alloy is a preferred material for some to be a standard method by ISO.7,8 This method may not suit all structural components in research nuclear reactors.
    [Show full text]
  • MEASURING KINETIC ISOTOPE EFFECTS of CARBON at NATURAL ABUNDANCE Reported by John D. Baird October 31, 2002 INTRODUCTION Crucial
    MEASURING KINETIC ISOTOPE EFFECTS OF CARBON AT NATURAL ABUNDANCE Reported by John D. Baird October 31, 2002 INTRODUCTION Crucial to understanding the selectivity of a reaction is knowledge of its mechanism and rate- limiting step. Methods used to study reaction mechanisms include: linear free-energy relationships,1 kinetic studies,2 solvent effect studies,3 and isotope effects.4 The measurement of kinetic isotopic effects (KIE) is a well-established and powerful tool for probing reaction mechanisms, and this method has been used to elucidate events taking place in the rate-limiting step of a wide range of reactions. Isotope effects are usually measured by kinetic competition reactions using isotopically labeled reactants. A common example is the observation of primary 2H KIEs to provide information regarding H transfer or secondary 2H KIE to investigate changes in hybridization at an adjacent carbon center. Kinetic isotope effects are not limited to the use of 2H, and KIEs of 13C have been used to determine whether fundamental bonding changes of carbon atoms are occurring in the rate-limiting step of a reaction. While these experiments provide useful information leading to fundamental knowledge in the mechanistic pathway of reactions, the synthesis of isotopically labeled carbon reactants and experimental design required for each reaction can be cumbersome, and the cost of enriched starting materials can be high. Since carbon exists as a mixture of isotopes, one alternative to the synthesis of 13C-labeled compounds is the use of materials at natural abundance. For example, high precision isotope ratio mass spectrometry (MS) of materials labeled at natural abundance can be used, but this technique relies on selective degradations (without isotopic fractionation) of materials into small molecules suitable for 5 (MS) analysis, such as CO2.
    [Show full text]
  • Isotope Distributions
    Isotope distributions This exposition is based on: • R. Martin Smith: Understanding Mass Spectra. A Basic Approach. Wiley, 2nd edition 2004. [S04] • Exact masses and isotopic abundances can be found for example at http: //www.sisweb.com/referenc/source/exactmaa.htm or http://education. expasy.org/student_projects/isotopident/htdocs/motza.html • IUPAC Compendium of Chemical Terminology - the Gold Book. http:// goldbook.iupac.org/ [GoldBook] • Sebastian Bocker,¨ Zzuzsanna Liptak:´ Efficient Mass Decomposition. ACM Symposium on Applied Computing, 2005. [BL05] • Christian Huber, lectures given at Saarland University, 2005. [H05] • Wikipedia: http://en.wikipedia.org/, http://de.wikipedia.org/ 10000 Isotopes This lecture addresses some more combinatorial aspect of mass spectrometry re- lated to isotope distributions and mass decomposition. Most elements occur in nature as a mixture of isotopes. Isotopes are atom species of the same chemical element that have different masses. They have the same number of protons and electrons, but a different number of neutrons. The main ele- ments occurring in proteins are CHNOPS. A list of their naturally occurring isotopes is given below. Isotope Mass [Da] % Abundance Isotope Mass [Da] % Abundance 1H 1.007825 99.985 16O 15.994915 99.76 2H 2.014102 0.015 17O 16.999131 0.038 18O 17.999159 0.20 12C 12. (exact) 98.90 13C 13.003355 1.10 31P 30.973763 100. 14N 14.003074 99.63 32S 31.972072 95.02 15N 15.000109 0.37 33S 32.971459 0.75 34S 33.967868 4.21 10001 Isotopes (2) Note that the lightest isotope is also the most abundant one for these elements.
    [Show full text]
  • Experimental Partitioning of Ca Isotopes and Sr Into Anhydrite: Consequences for the Cycling of Ca and Sr in Subseafloor Mid-Ocean Ridge Hydrothermal Systems
    Lawrence Berkeley National Laboratory Recent Work Title Experimental partitioning of Ca isotopes and Sr into anhydrite: Consequences for the cycling of Ca and Sr in subseafloor mid-ocean ridge hydrothermal systems Permalink https://escholarship.org/uc/item/5cf1x0d9 Authors Syverson, DD Scheuermann, P Higgins, JA et al. Publication Date 2018-09-01 DOI 10.1016/j.gca.2018.03.018 Peer reviewed eScholarship.org Powered by the California Digital Library University of California Available online at www.sciencedirect.com ScienceDirect Geochimica et Cosmochimica Acta xxx (2018) xxx–xxx www.elsevier.com/locate/gca Experimental partitioning of Ca isotopes and Sr into anhydrite: Consequences for the cycling of Ca and Sr in subseafloor mid-ocean ridge hydrothermal systems Drew D. Syverson a,b,c,⇑, Peter Scheuermann b, John A. Higgins d, Nicholas J. Pester e, William E. Seyfried Jr. b a Yale University, Department of Geology and Geophysics, 210 Whitney Ave., New Haven, CT 06511, USA b University of Minnesota, Department of Earth Sciences, 310 Pillsbury Drive SE, Minneapolis, MN 55455-0231, USA c Monash University, Department of Earth, Atmosphere and Environment, 9 Rainforest Walk, Building 28, Clayton, VIC 3800, Australia d Princeton University, Department of Geosciences, Guyot Hall, Princeton, NJ 08544, USA e Lawrence Berkeley National Laboratory, One Cyclotron Road, Berkeley, CA 94720, USA Received 2 August 2017; accepted in revised form 20 March 2018; available online xxxx Abstract The elemental and isotopic mass balance of Ca and Sr between seawater and the oceanic crust at mid-ocean ridge (MOR) hydrothermal systems integrates various physiochemical processes in the subseafloor, such as dissolution of primary silicate minerals, formation of secondary minerals, and phase separation in the subseafloor.
    [Show full text]
  • Natural Abundance D N and D C of DNA Extracted from Soil
    ARTICLE IN PRESS Soil Biology & Biochemistry 39 (2007) 3101–3107 www.elsevier.com/locate/soilbio Natural abundance d15N and d13C of DNA extracted from soil Egbert Schwartza,d,Ã, Steven Blazewicza, Richard Doucettb, Bruce A. Hungatea,b,d, Stephen C. Hartc,d, Paul Dijkstraa,d aDepartment of Biological Sciences, Northern Arizona University, P.O. Box 5640, Flagstaff, AZ 86011, USA bColorado Plateau Stable Isotope Laboratory, Northern Arizona University, P.O. Box 5640, Flagstaff, AZ 86011, USA cSchool of Forestry, Northern Arizona University, P.O. Box 5018, Flagstaff, AZ 86011, USA dMerriam-Powell Center for Environmental Research, Northern Arizona University, P.O. Box 5640, Flagstaff, AZ 86011, USA Received 24 April 2007; received in revised form 27 June 2007; accepted 8 July 2007 Available online 6 August 2007 Abstract We report the first simultaneous measurements of d15N and d13C of DNA extracted from surface soils. The isotopic composition of DNA differed significantly among nine different soils. The d13C and d15N of DNA was correlated with d13C and d15N of soil, respectively, suggesting that the isotopic composition of DNA is strongly influenced by the isotopic composition of soil organic matter. However, in all samples DNA was enriched in 13C relative to soil, indicating microorganisms fractionated C during assimilation or preferentially used 13C enriched substrates. Enrichment of DNA in 15N relative to soil was not consistently observed, but there were significant differences between d15N of DNA and d15N of soil for three different sites, suggesting microorganisms are fractionating N or preferentially using N substrates at different rates across these contrasting ecosystems. There was a strong linear correlation between d15N of DNA and d15N of the microbial biomass, which indicated DNA was depleted in 15N relative to the microbial biomass by approximately 3.4%.
    [Show full text]
  • Cr(VI) Standard Solution. 0.0029 G of Cr2o3 ( Cr Enriched Isotope) Was
    Electronic Supplementary Material (ESI) for Journal of Analytical Atomic Spectrometry This journal is © The Royal Society of Chemistry 2012 Preparation of enriched isotopic and natural abundance standard solutions 50 50 Cr(VI) standard solution. 0.0029 g of Cr2O3 ( Cr enriched isotope) was transferred to a platinum beaker and 0.4 g of NaKCO3 and 0.1 g of NaOH were added. The contents were melted by a Bunsen burner until a yellow-orange melt was obtained. During the melting procedure quantitative oxidation of Cr by air oxygen was achieved only in an alkaline media. The melt was cooled to a room temperature and 0.7 mL of concentrated HCl was carefully added to dissolve the deposit. The clear solution was transferred to a Teflon tube and diluted to 10 mL with water.1 The concentration of Cr in the stock isotopic spike solution was determined by reverse ID-ICP-MS and found to be 197.2 ± 0.8 μg mL-1. 53 53 Cr(III) standard solution. 0.0029 g of Cr2O3 ( Cr enriched isotope) was transferred to a Teflon vessel and 4 mL of concentrated HNO3 was added. The Teflon vessel was subjected to microwave assisted digestion performed at maximal power of 1200 W, ramp to temperature 20 min, 190 oC, pressure 10 bar, holding 20 min, cooling 20 min. The clear solution was quantitatively transferred to a platinum beaker and the contents carefully evaporated to approximately 0.2 mL. Then 0.7 mL of concentrated HCl was added, the solution transferred to a Teflon tube and diluted to 10 mL with water.1 The concentration of Cr in the stock isotopic spike solution was determined by reverse ID-ICP-MS and found to be 200.3 ± 0.9 μg mL-1.
    [Show full text]