Detection of Uranium in a Very Hard Water Matrix Using Ultrasonic Nebulization with ICP-AES Detection December 3, 2015.

Slides:



Advertisements
Similar presentations
A Modern Approach to Controlling ICP Spray Chamber Temperature Jerry Dulude, Glass Expansion,
Advertisements

Elemental Spectroscopy ICP-OES
Ion Sources Some characteristics of ion sources (especially in high precision work): It should have high efficiency in generating ions of the element of.
Chapter 10 ATOMIC EMISSION SPECTROMETRY
Atomic Emission Spectroscopy
Inductively Coupled Plasma Mass Spectrometry or ICP-MS
IDDepth δ 13 CCarbonNitrogenδ 13 C Depth: (cm)(‰)(%) (‰)(cm) Gr. 3-5A %0.17% Gr %0.12% Gr %0.09%
HL Chemistry - Option A: Modern Analytical Chemistry ATOMIC ABSORPTION SPECTROSCOPY.
Flame photometry.
Printed by Approaching a Universal Pneumatic Nebulizer – the next step Jerry Dulude and Ron Stux (USA), Vesna Dolic and Peter Liddell.
Atomic Emission Spectroscopy
427 PHC.  Atomic emission spectroscopy (AES) is based upon emission of electromagnetic radiation by atoms.
Printed by Approaching a Universal Pneumatic Nebulizer Jerry Dulude (USA), Vesna Dolic and Peter Liddell (Australia), Glass Expansion.
Temperature-Related Stability in Plasma Spectrometry Jerry Dulude, Ron Stux, and Vesna Dolic, Glass Expansion,
Applications of Analytical Chemistry at RTI International  Argon plasma instruments Atomic Emission (ICP-AES) – 3 Quadrupole Mass Spectrometers (ICP-MS)
ATOMIC EMISSION SPECTROMETRY Chap 10 Sections: Sections: 10A 10A 10A-1 10A-1 10A-3 (skim) 10A-3 (skim) 10A-4 10A-4.
Applied Water and Spent water Manual Chapter 14
Detection of Copper in Wastewater Seth Holm Chem4101 December 2009.
Exp. 15: Volumetric Analysis: Total Hardness of Water by EDTA
Agilent 7500 ICP-MS Date: 28JUL2005.
Look at your mineral water label Where do the dissolved minerals come from? How do you think the minerals affect the water?
Atomic Emission Spectroscopy
Atomic Emission Spectrometry
Materials Characterization Lab Elemental Analyses by ICP-AES Henry Gong, Senior Analytical Chemist September 10, 2008.
Mg + N 2  Mg 3 N 2 Pb + Ag +  Pb 2+ + Ag Magnesium metal is burned in nitrogen Lead foil is immersed in silver nitrate A solution of ammonium sulfate.
Unit 08b : Advanced Hydrogeology Groundwater Chemistry.
Marcellus Shale Wastewaters Management by Resource Recovery Shale Gas Innovation Contest Ben Franklin Technology Partners April 13, 2012 Timothy Keister,
The Bruker ICP-MS – a Versatile Tool for Sensitive and Interference Free Analysis of Different Matrices Title of sales presentation – Remarks: „Bruker.
Hardness Objective n to understand the chemical basis of water hardness, how it originates, and ways it can affect water distribution systems. n to know.
In arid and semi-arid regions, agriculture is limited by the availibility of suitable irrigation water. Groundwater is the main source of irrigation and.
The determination of lead by MD-HG-AFS in APMP*-QM-P3 comparison Lu Xiaohua, Lu Hai, Ma Liandi, Cui Yanjie National Research Center for Certified Reference.
Sulfates Presentation By Douglas Rittmann, Ph.D., P.E. Water/Wastewater Consultant To CE 4153 Lab Course On February 7, 2006.
Inductively Coupled Plasma-Optical Emission Spectrometry (ICP-OES) Figure 1. The Varian Vista-PRO CCD Simultaneous ICP-OES in the Physical Geography laboratories.
in tin pest and pest free Monika Leodolter-Dvorak and Ilse Steffan
1.1 Inductively coupled plasma (ICP) Three Argon flow 1.Plasma gas (10-20 L/min) 2.Nebulizer gas (~1L/min) 3.Optional auxiliary gas (~0.5L/min) Radio-frequency.
Atomic Absorption Spectroscopy
16 Dissolved Mass in Groundwater Hydrochemistry. Introduction Water Chemistry: Origin of water Uses of water Water quality (contamination) Topics: 16.1Dissolved.
Atomic Absorption Spectrometer Varian SpectrAA Model 220FS.
Effect of Sample Introduction on ICP-MS Detection of Nonmetal Analytes in a Simulated HPLC Matrix Adam E. Dill and Jon W. Carnahan Department of Chemistry.
Classification used for health risk estimate interpretation and map visualization CHRONIC RISK CANCER RISK Health risk estimate 29 th International.
Nutrients  Why monitor nutrients? –Plant and algae growth  Carbon, nitrogen, phosphorus, oxygen, silica, magnesium, potassium, calcium, iron, zinc, and.
COMPARISON OF DIFFERENT ANALYTICAL TECHNIQUES FOR ENVIRONMENTAL MONITORING OF CONTAMINATED SOILS Metodi Mladenov, Daria Ilieva University of Chemical Technology.
A UNIVERSAL PROGRAMMABLE TEMPERATURE SPRAY CHAMBER Jerry Dulude, Glass Expansion,
Adv. Inst. Techs.  flame emission (eg flame photometer) known as low temperature emission ( K) ◦ first form of spectroscopy ◦ used in commercial.
ATOMIC SPECTROMETRY 1. Flames 2. Electrothermal Atomizers 3. Plasmas.
ICP MAKING STANDARDS. NUMBER OF STANDARDS Determine the number of standards necessary for your measurements (Blank, 100ppb, 500ppb, 1000ppb, etc)
SPRAY CHAMBER TEMPERATURE: A CRITICAL (YET OFTEN MISSING) PARAMETER IN ICP EXPERIMENTS Jerry Dulude, Ron Stux, and Vesna Dolic, Glass Expansion,
The Islamic University of Gaza- Environmental Engineering Department
Printed by A New Versatile Programmable Temperature Spray Chamber for ICP Jerry Dulude and Ron Stux (USA), Vesna Dolic (Australia),
Chapter 5 (CIC) and Chapter 18 (CTCS) Read in CTCS Chapter Problems in CTCS: 18.33, 35, 37.
Atomic-absorption spectroscopy
Brianna Shildt & Kirsten Berube.  A poisonous metal  Its found naturally in soil and minerals  Arsenic compounds are used as pesticides.  There is.
Minimization of matrix effects with environmental samples using ICP-OES.
A Comparison of EPA Method and ASTM D6239 for Uranium in Hard Water Matrices Robert L. Metzger & Pierre Pouquette.
Abstract Analysis of organic solvents by ICP is often seen as problematic and challenging due to the nature of the solvents used. Commonly encountered.
Associate Prof. Meral TOPCU SULAK
An in-depth look at trace metallic impurity determination by ICP-OES
Satish Pradhan Dnyanasadhana College Department Of Chemistry
Flame Emission Spectrometry
The ratio of excited state to ground state atoms as a function of temperature is determined by the Maxwell-Boltzmann expression. Fig Excited state.
Determination of Water Hardness
COMPARISON OF EXCITATION CONDITIONS IN
Michael Raessler, Jan Rothe and Ines Hilke
UGRC 144 Science and Technology in Our Lives/Geohazards
Strategies for Eliminating Interferences in Optical Emission Spectroscopy Best practices to optimize your method and correct for interferences to produce.
The Analysis of Soils and Waters in Accordance with U. S
Ultimate Clean Digestion Cups and Clean Lab Testing
بر اساس جدول تناوبی از یک جایی به بعد فلزات سنگین قرار دارند
Satish Pradhan Dnyanasadhana College Department Of Chemistry
Atomic Absorption Spectroscopy. Atomic absorption spectroscopy is based on the same principle as the flame test used in qualitative analysis.
Presentation transcript:

Detection of Uranium in a Very Hard Water Matrix Using Ultrasonic Nebulization with ICP-AES Detection December 3, 2015

Introduction Uranium is a regulated element in drinking water per the USEPA guideline of an MCL (maximum contaminant level) of 30 micrograms per liter. Human health risks from long-term exposure to elevated uranium levels in drinking water can include impaired kidney function and cancer. Uranium in groundwater can occur from natural leaching of mineral deposits; subsequent very hard water matrices are present in areas such as southeastern United Kingdom and southern Germany. This presentation will examine the utility of coupling an ultrasonic nebulizer (USN) with an ICP-AES instrument for improved detection of uranium in a simulated very hard water matrix.

Uranium Human Health Concerns Heavy Metal –Impaired kidney function (nephritis) Radionuclide –Alpha emitter 238 U 234 Th + α α = 4 He 2

Uranium Sources in the Environment Mineral deposits Mining Burning of coal Emissions from nuclear power plants Munitions Phosphate fertilizers

Hard Water Dissolved solids content of groundwater can vary upon exposure to mineral deposits such as calcium and magnesium carbonate. “Hard water” designation describes water that is hard to use with soap (less formation of soap lather) Units used to describe the extent of water hardness include: –Degrees of General Hardness (dGH) –Grains per Gallon –German Degrees (°dH) –English Degrees or °Clark –French Degrees (°fH) –Parts per million (mg/L as CaCO 3 ) Note: 1 grain = 64.8 mg CaCO 3

Hard Water – Definition of Units United States Geological Survey (USGS) –Soft 0 to 60 mg/L (ppm) –Moderately Hard 61 to 120 mg/L (ppm) –Hard 121 to 180 mg/L (ppm) –Very Hard > 181 mg/L (ppm) Web Link: Hardness as mg/L CaCO 3.

United Kingdom Map – Hard Water UK Map Source: Wikipedia Harder water is generally observed to the right of the blue line. Newcastle Exeter Detailed UK Hard Water Map:

United Kingdom Map – Uranium in Water UK Map Source: Wikipedia Detailed UK Uranium in Water Map: B.Smith, P.L.Smedley, C. Abesser, D. Lapworth, Uranium Occurrence And Behavior in British Groundwater, British Geological Survey Commissioned Report, CR/06/050N Central Lowlands West Midlands Region

Germany Map – Hard Water Germany Map Source: FreeVectorMaps Hard water areas include NW Germany and southern Germany. Mecklenburg – Vorpommern Baden- Wurttemburg Bayern Detailed Hard Water Map of Germany:

Germany Map – Uranium in Water Germany Map Source: FreeVectorMaps Detailed Information for Uranium in Waters in Germany: Uranium in German Tap and Groundwater – Occurrence and Origins in The New Uranium Mining Boom, Merkel B. and M.Schipek, Eds., Springer. Berlin, Thuringen Sachsen

United States of America Map – Hard Water Omaha USA Map Source: FreeVectorMaps States marked have more areas of hard or very hard water Detailed hard water map of USA: TX OK CO WY UT KS AZ NM CA NE

United States of America Map – Uranium in Water USA Map Source: FreeVectorMaps High Plains Aquifer: SD, NE, WY, CO, KS, OK, NM, TX Central Valley Aquifer: CA Detailed Uranium in Groundwater Map: J. Dolan, K.A. Weber, Natural Uranium Contamination in Major U.S. Aquifers Linked to Nitrate, Environ.Sci.Technol.Lett., 2, , CA NE KS CO OK TX SD WY NM

Selected Drinking Water Standards for Uranium Entity or Country Uranium Limit (  g/L) WHO30 Australia20 Canada20 Germany10 USEPA30 Notes: WHO limit based on consumption of 2 Liters of water per day and a human weight of 60 kg. There is a provisional WHO limit of 15  g/L U. An additional German standard is 2  g/L for water used for preparation of baby food.

Equipment ICP-AES Instrument – PerkinElmer 5300DV ICP-MS Instrument –ThermoFisher iCAP Q Ultrasonic Nebulizer –Teledyne CETAC U5000AT +

Instrument Detection Limits: Uranium ICP-AES – 1 to 10  g/L Possible need for pre-concentration of U by chelation ICP-MS – 0.1 ng/L R.Thomas, Practical Guide to ICP-MS 3 rd Ed., CRC Press, New York, 2013.

Emission Wavelengths Uranium – nm – nm – nm – nm – nm Decreasing Intensity

Ultrasonic Nebulizer – Front View

Ultrasonic Nebulizer Principle of Operation In place of a regulated gas flow for generation of a liquid sample aerosol (pneumatic nebulization), liquid sample is pumped across an oscillating (piezoelectric) crystal. The oscillations will cause formation of a sample aerosol. Ultrasonic nebulization is typically 10-15% efficient for conversion of liquid sample into a useable aerosol. An in-line desolvation system is used to prevent plasma overloading with water vapor and maintain ICP stability. Note that the host ICP-AES / ICP-MS nebulizer gas now acts as a carrier gas, moving the generated aerosol to the plasma.

Ultrasonic Nebulizer – Schematic Transducer Assembly

Transducer – Close-Up View Piezoelectric Disk Quartz Faceplate

Ultrasonic Nebulizer – Top View Heated J-Tube Condenser

Ultrasonic Nebulizer with ICP-AES

Operating Conditions - I ICP-AES: PE Optima 5300DV ICP RF Power: 1350 W Plasma Gas: 15 L/min Auxiliary Gas:0.2 L/min Nebulizer Gas:0.62 L/min Viewing:Axial Torch Injector:Alumina, 2.0 mm i.d. Torch Position:-2 Nebulizer: Glass concentric Spray Chamber: Glass cyclonic Resolution:Normal Points/peak:3 Integration time: 20s, 3 replicates

Operating Conditions - II Nebulizer System:CETAC U5000AT + Heater Temp: 140°C Cooler Temp: 3°C Torch position: -4 Nebulizer Gas:0.52 L/min Solution Uptake: 2.0 mL/min (pumped)

U5000AT + Setup – Front View Nebulizer Gas Line Sample Out Line With Torch Adapter

U5000AT + Setup – Back View Nebulizer Gas Line Sample Out Line Drain Pump

Very Hard Water Matrix* Calcium: 500 mg/L Magnesium: 200 mg/L Sodium: 200 mg/L Potassium: 200 mg/L Iron: 200 mg/L *Made from single-element 10,000 mg/L ICP grade standards.

Tapwater Matrix ElementWavelength (nm)Concentration (mg/L) Na / K / Ca / Mg / Uncertainty is 2  Municipal water source, Omaha, NE Conversion of the mg/L Ca to mg/L CaCO 3 gives ~123 mg/L CaCO 3 classifying this tapwater sample as hard water. An approximate uranium concentration of 4.2  g/L measured by ICP-MS using a 1-pt standard addition.

Evaporated Water Samples Deionized Water Omaha, NE Tapwater Estuarine Water (St.Lawrence Seaway) V. Hard Water Matrix

Experiment Details 1. A matrix blank and four calibration standards (matrix-matched) were prepared using the 10,000 mg/L single element standards, preserved in 1% high-purity nitric acid. 2. Four calibration standards were prepared: 20, 50, 100 and 200  g/L. No internal standard was used. 3. The matrix blank and matrix-matched standards were introduced to the standard concentric nebulizer and the U5000AT + using the on-board peristaltic pump of the host ICP-AES. 4. Instrument detection limits (IDLs) are 3x the standard deviation of the matrix blank concentration; limits of quantitation (LOQs) are 10x the standard deviation of the matrix blank concentration. 5. The 100  g/L standard was reintroduced to measure % recoveries.

Maximum Contaminant Levels (MCLs) for USEPA Regulated Elements Element MCL in  g/L As10 Ba2000 Be4 Cd5 Cr100 Cu1300 Pb15 Sb6 Se50 Tl2 U30

Uranium nm Ca and Fe Interference 200 ppb U 200 ppm Fe, 500 ppm Ca U5000AT + USN

Uranium nm Iron Interference 200 ppm Fe 200 ppb U U5000AT + USN

Uranium Detection w. ICP-AES Very Hard Water Matrix Mixed results in generating interelement correction factors (IECs) for the nm and nm U emission lines Attempt to use one or more of the less sensitive U emission lines –Enhance signal with ultrasonic nebulization

Uranium nm Probable Ca Interference ( nm) U5000AT + USN Saturated

Uranium nm Calibration Standards in Very Hard Water 20, 50, 100, 200 ppb U In very hard water U5000AT + USN

Uranium nm Calibration Standards in Very Hard Water 20, 50, 100, 200 ppb U In very hard water U5000AT + USN

ICP-AES Intensity Comparison Very Hard Water Matrix, 100  g/L ElementWavelength (nm) Std NebulizerU5000AT+Factor As , Ba ,2414,756, Be ,5372,217, Cd ,43357, Cr ,82880, Cu ,529135, Pb ,5887, Sb , Se , Tl , U ,45013, U ,25810,6748.4

Uranium nm Calibration in Very Hard Water U5000AT + USN 20, 50, 100, 200 ppb U

Uranium nm Calibration in Very Hard Water U5000AT + USN 20, 50, 100, 200 ppb U

Standard Concentric Nebulizer Very Hard Water Matrix ElementWavelength (nm) IDL (  g/L)LOQ (  g/L) %Recovery As Ba Be Cd Cr Cu Pb Sb Se Tl U

U5000AT + Ultrasonic Nebulizer Very Hard Water Matrix ElementWavelength (nm) IDL (  g/L)LOQ (  g/L) %Recovery As Ba Be Cd Cr Cu Pb Sb Se Tl U U

ICP-AES LOQ Comparison Very Hard Water Matrix ElementWavelength (nm) Std Nebulizer (  g/L) U5000AT+ (  g/L) Factor As Ba Be Cd Cr Cu Pb Sb Se Tl U

Uranium nm Calibration in Very Hard Water U5000AT + USN 10, 20, 50, 100 ppb U

Uranium nm Calibration in Very Hard Water U5000AT + USN 10, 20, 50, 100 ppb U

Uranium Detection Limits Very Hard Water Matrix ElementWavelength (nm) IDL (  g/L)LOQ (  g/L) % Recovery U U U5000AT + USN % Recovery of 10  g/L standard Use 10, 20, 50, 100 ppb U standard spikes

Summary ICP-AES with ultrasonic nebulization can detect 10  g/L U in a very hard water matrix Uranium emission wavelengths are chosen to avoid interferences from Ca and Fe, with ultrasonic nebulization providing sufficient sensitivity for less intense U emission lines