In-situ measurements of CO2

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In-situ measurements of CO2 Calibration, error estimates, role of in-situ chemical measurements, quantification of fossil fuel emissions Pieter Tans NOAA Earth System Research Laboratory 3 March 2010 Keck Workshop on Quantifying the Sources and Sinks of Atmospheric CO2

Requirements for our greenhouse gas measurements Goals of GHG observing system in today s environment: 1. Provide independent assessment of emissions reductions 2. Monitor & understand the carbon cycle, improve prognoses Measurements should be accepted as fully trustworthy, implying complete and prompt disclosure of all results, including data flagged as bad Disclosure is not an afterthought. It takes people and resources All measurements have to be proven to be comparable All reported measurements should be accompanied by defensible uncertainty estimates. Defensible uncertainty estimates require a considerable amount of duplication Uncertainty includes systematic errors that vary in time and are poorly understood

Some definitions in metrology: Requirements for our greenhouse gas measurements Measurement: Process of experimentally obtaining a quantity value that can reasonably attributed to a quantity Note: Any measurement is a comparison with a measurement standard Measurand: Quantity intended to be measured (mole fraction in dry air) Note: A measurement includes the collection of a sample and its pretreatment, such as drying. Measurement result: Set of quantity values attributed to a measurand, together with any other available relevant information Note: In most cases a measurement result has to include an estimate of its uncertainty, taking into account all known contributions, not just a statistical estimate of repeatability. Measurement error: Measured quantity value minus a reference quantity value Measurement precision: Closeness of agreement of replicate measurements under specified conditions: 1. repeatability: same operators, same equipment and procedure, same location, same conditions, over relatively short time 2. reproducibility: different operators, equipment, procedure, location, conditions, and over extended time period. Comparability: Measurement results are comparable if they are metrologically traceable to the same reference Traceability: result is related to a reference through a documented unbroken chain of calibrations Sources: VIM3 (2008); De Bièvre, Metrologia, 2008

WMO Mole Fraction Scale for CO2 (X2007) Comparisons with other primary scales, gravimetric etc. 15 WMO Primary manometric 20 additional manometric reference gas mixtures CO2 in air mixtures CO2 in air, range 230-520 ppm range 75-3000 ppm transfer by any suitable analytical method 16 secondaries range 250-530 ppm 1 target cylinder 3-4 working per site standards per site

WMO Mole Fraction Scale for CO2 (X2007)

WMO Mole Fraction Scale for CO2 (X2007)

WMO Mole Fraction Scale for CO2 (X2007) Internal consistency of the scale, X2001

WMO Mole Fraction Scale for CO2 (X2007) recent thistory of fthe WMO scale

WMO Mole Fraction Scale for CO2 (X2007) Comparison of NIES gravimetric standards with WMO-X2005 Cylinder NIES ESRL ESRL NDIR mano May 05 July 06 July 06 30089 350.14 350.21 350.15 30091 350.02 350.03 350.03 30092 390.11 390.09 390.10 30093 390.11 390.0909 390.15 30094 389.03 389.02 389.02 NIES data courtesy of Yasunori Tohjima

WMO Mole Fraction Scale for CO2 (X2007) 771 comparisons mean absolute difference 0.015 ppm 950 comparisons mean absolute difference 0.016 ppm Duane Kitzis (ESRL), statistics since 2004

Uncertainty estimates of in-situ measurements

Conclusions: Uncertainty estimate of WMO X2007 scale is 0.14 ppm (2 sigma), which is consistent with independent scales. Uncertainty of the propagation of the scale is 0.04 ppm (2 sigma) Full uncertainty of air measurements: Slowly varying biases mostly related to air handling (often not understood) <0.3 ppm (2 sigma)

Role of in-situ measurements

Role of in-situ measurements

Role of in-situ measurements

Role of in-situ measurements

Role of in-situ measurements In-situ profile tropopause AirCore ground

Role of in-situ measurements In-situ profile AirCore profile AirCore profile AirCore mean AIRS retrieval OCO retrieval FTS retrieval

Conclusions: Chemically stable in the atmosphere, CO2 is an excellent tracer for atmospheric transport. Independent methods (measurements, models) are necessary to provide a more realistic estimate t of uncertainty t of source/sink estimates. t In-situ full profile measurements are needed on an ongoing basis to discover and diagnose biases of remote sensing, so that retrieval algorithms can be improved.

Verification of emissions E ( mol / s ) fetch ( area ) ΔX = area w( m / s) 1 column( mol / 2 m ) Estimates of typical CO2 increases (ΔX) due to fossil fuel combustion: (average, downwind side of area, 5 m s-1 wind, BL height 1 km) U.S. 0.8 ppm (column) 3 ppm (BL 2 km) Germany 0.6 5 Indonesia 0.1 1 S. Korea 0.6 5 Houston 0.7 6 Beijing 1.1 9 Shanghai 1.8 15

Verification of emissions Observing system simulation experiment: 10,000 14 CO 2 samples/year, one every 3 days in every grid point below, Lagrangian back-trajectories, measurement error 2 permil or 0.7 ppm of recent fossil fuel CO2. John Miller (ESRL)

Verification of emissions CO2 vs. anthropogenic gases blue: winter red: summer John Miller, ESRL

Verification of emissions Observed emissions ratios: m=19 ppb/ppm m=12 ppb/ppm Red=Summer Blue=Winter m=7.2 ppt/ppm m=3.0 ppt/ppm m=1.2 ppt/ppm m=1.2 ppt/ppm m=4.0 ppb/ppm m=2.3 ppb/ppm m gas x E ff = E gas Recent fossil component of CO2 John Miller, ESRL

Verification of emissions USA Emission Estimates 400 Gg; Tg CO O; 0.1 Gg SF6 350 300 250 200 150 100 50 14CO2 EPA 0 CO SF6 HFC134a HCFC22 HCFC142b PCE CH2Cl2 C6H6 John Miller, ESRL

Verification of emissions Down wind of Indianapolis, November 2008 Paul Shepson, Purdue

Conclusions: 14 CO2 measurements separate CO2 from recent fossil fuel burning from natural sources/sinks, making 14 C a clean tracer for fossil fuels. 5000 14 C samples per year would quantify regional fossil fuel CO2 to ~10% on regional scales, if there is no transport t error. Initially use 14 C tracer to improve transport as long as we can trust inventories. Correlate 14 CO2 depletion with other species, to quantify emissions from other species. They in turn can help fossil fuel quantification in fairly remote areas where 14 CO2 depletion is very dilute. 14 CO2 measurements extract a clean seasonal cycle signal from terrestrial ecosystems