N A A D C A 1942 G E U E O Q ASITA-2014 L I G O O G L I O C A É G L S N U O R I V S E S Y I M - M C O A Triple-Ratios Characterization of Nitrogen- Containing Compounds in Atmospheric samples from Alberta Using Chemical Conversion and Thermal Decomposition of N 2 O Anna Smirnoff 1 , Martine M. Savard 1 , Robert Vet 2 , and Marie-Christine Simard 1 1 Geological Survey of Canada, 490 rue de la Couronne, Quebec (Quebec), G1K 9A9 2 Environment Canada 4905 Dufferin Street Toronto (Ontario), M3H 5T4
N A A D C A 1942 G E U E O Q Objectives L I G O O G L I O C A É G L S N U O R I V S E S Y I M - M C O Project “SOURCES” ( SOurce apportionment Using isotope Ratio Characterization of oil sands Environmental Samples) : Better understand the terrestrial N cycle and the fate of atmospheric N-species Presentation Characterize the 4 main sources of O-bearing airborne N contaminants in 4 Albertan settings
N A A D C A 1942 NO x Souces in Northern G E U E O Q L I G O O G L I O C Alberta A É G L S N U O R I V S E S Y I M - M C O Atmospheric sources of nitrogen-bearing compounds Characterized by δ 15 N, δ 17 O and δ 18 O Desulphurization and hydrogen plants, boilers, heaters, turbines, vehicles, etc. OS Operations Gas Coal-Fired Agriculture Transport Upgraders compressors Power Plants and gas plants
N A A D C A 1942 G E U E O Q L I G Sample Types O O G L I O C A É G L S N U O R I V S E S Y I M - M C O Sample type Sampler Directional - NO 3 Wet-only No + NH 4 Wet-only No Gaseous NH 3 Filterpack (citrated cellulose) Yes Particle NO 3 - Filterpack (Teflon) Yes Particle HN 4 + Filterpack (Teflon) Yes Gaseous NO 2 and NO x Maxxam (Resins) No Gaseous HNO 3 Filterpack (Nylon) Yes 4
N A A D C A 1942 G E U E O Q Analytical Approach L I G O O G L I O C A É G L S N U O R I V S E S Y I M - M C O Characterize nitrogen compounds using triple oxygen and nitrogen isotopic ratios: Collect various nitrogen compounds in wet, dry and gaseous forms at different locations Convert all samples into solution for further treatment Convert all N-species into one form (NO 2 - ) Convert NO 2 - into N 2 O Decompose N 2 O into N 2 and O 2 Obtain results for δ 15 N, δ 17 O, δ 18 O Normalize results using International standards
N A A D C A 1942 Sampling Area 1: G E U E O Q L I G O O G L I O C A É (Southwest of Edmonton) G L S N U O R I V S E S Y I M - M C O Sundance Keephills Genesee Alberta coal-fired power plants emissions 6
N A A D C A Sampling Area 2: 1942 G E U E O Q L I G O O G L I O C A É (Vauxhall, SW Alberta) G L S N U O R I V S E S Y I M - M C O - ) Gas compressor stations (NO x and NO 2 7
N A A D C A 1942 Sampling Area 3: G E U E O Q L I G O O G L I O C A É (Edmonton) G L S N U O R I V S E S Y I M - M C O 359 o Terrace Heights, City of Edmonton sampling Sector Sundance Sewage Treatment Plant Keephills Airport Genesee 210 o City/Traffic emissions
N A A D C A 1942 Sampling Area 4: G E U E O Q L I G O O G L I O C A É (Fort Saskatchewan) G L S N U O R I V S E S Y I M - M C O 20° 354° 267° 9 Emissions from Upgraders facilities
N A A D C A 1942 G E U E O Q L I G Sample Preparation O O G L I O C A É G L S N U O R I V S E S Y I M - M C O Very few labs can analyze triple oxygen and nitrogen… Methods of sample preparation and analysis are described in article published in 2012 in “Rapid Communications in Mass Spectrometry” The procedure can be divided into a few major steps 10
N A A D C A Sample Preparation using 1942 G E U E O Q L I G O O G L I O C A É Chemical Approach G L S N U O R I V S E S Y I M - M C O 10 cm 5-cm ID 85 mL Conversion of NO 3 - to NO 2 - (passing sample through Cd- reduction column) 2-mm ID Reduce NO 2 - to N 2 O using NaN 3 25 cm (sodium azide) 18.5 cm 3.5-mm ID Analyze N 2 O using our modified Pre-Con with a gold furnace Cu-Cd granules Glass wool plug 11
N A A D C A 1942 G E U E O Q Analytical Setup L I G O O G L I O C A É G L S N U O R I V S E S Y I M - M C O vent vent vent To IRMS He water trap Mg(ClO 4 ) 2 MoleSieve GC Column, 30m Valco 6 port He Mg(ClO 4 ) 2 + NaOH RT-Q Bond Plot, 15m He auto auto manual U U U Gold LH 2 LH 2 LH 2 Furnace Pre-Con Modified from Brand,1995
N A A D C A 1942 G E U E O Q L I Results from the system G O O G L I O C A É G L S N U O R I V S E S Y I M - M C O
N A A D C A Dual Isotope Results 1942 G E U E O Q L I G O O G L I O C A É Particulates and Gases G L S N U O R I V S E S Y I M - M C O δ 15 N vs δ 18 O in NO 3 (HNO 3 -gas) 90 Vauxhall, Gas copr. Genesee, CFPP 80 Fort Sask. δ 18 O 70 60 50 Terr. Heights, URBAN 40 30 -10 -8 -6 -4 -2 0 2 4 6 8 10 δ 15 N δ 15 N vs δ 18 O in NO 3 (particulates ) 90 80 Vauxhall, Gas copr. Genesee, CFPP δ 18 O 70 Fort Sask. 60 50 Terr. Heights, URBAN 40 Fort Sask. 30 -8.0 -6.0 -4.0 -2.0 0.0 2.0 4.0 6.0 8.0 10.0 12.0 δ 15 N
N A A D C A Triple Isotope Results for 1942 G E U E O Q L I G O O G L I O C A É G (Gaseous and Particulates) L S N U O R I V S E S Y I M - M C O - in particulates - gases NO 3 HNO 3 - (particulates) NO 3 (gas) HNO 3 Genesee, CFPP Genesee, CFPP Genesee, CFPP Vauxall, Gas Comp. Vauxall, Gas Comp Terrace Heights, Fort Saskat., Urban Upgraders Terrace Heights, Urban Fort Saskat., Upgraders
N A A D C A 1942 G E U E O Q Conclusions L I G O O G L I O C A É G L S N U O R I V S E S Y I M - M C O Triple isotope characterization offers a great potential for distinguishing N-sources: coal-fired plants urban transportation upgraders Potential for understanding modification processes and fate of N contaminants
N A A D C A 1942 G E U E O Q The End L I G O O G L I O C A É G L S N U O R I V S E S Y I M - M C O C’est tout!
Recommend
More recommend