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Measurement techniques and data analysis Instrument descriptions Space instruments What does a data set tell us?
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Ozone instruments Chemical cell: 2H + + 2I - + O 3 I 2 + O 2 + H 2 O Variant: ECC ozone sondes Electromagnetic force derived from KI solution in two different concentrations (0.06 Mol/l and >8 Mol/K). Ozone flows through cell with lower conc. and releases free iodine according to 2KI + O 3 + H 2 O I 2 + O 2 + 2KOH. The iodine is converted to 2I - at the Pt cathode (and 2I - are converted to I 2 at the anode) producing an electrical current, which is then measured.
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Ozone instruments O 3 absorption cross section ~ 1.2·10 -18 cm 2 at 258 nm UV absorption
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Ozone instruments chemoluminescence spectrum O 3 + C 2 H 4 HCHO* + other HCHO* HCHO + h Chemoluminescence
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NO x instruments Chemoluminescence NO + O 3 NO 2 * + O 2 + other NO 2 * NO 2 + h Photolytic converter In order to measure NO 2, a photolytic converter is used in front of the CLD to convert NO 2 to NO
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HO x instruments LIF (laser induced fluorescence) Radical converter In order to measure HO 2, a gas flow of NO is added to the sample so that HO 2 +NO OH+NO 2
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Hydrocarbon instruments Gas chromatography For most gases, a cryogenic preconcentration is required
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Sample gas chromatogram
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CO, CO 2 instruments Gas correlation radiometer c proportional to ln(I/I 0 )
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spectroscopy instruments DOAS (differential optical absorption spectroscopy) 1 2 I1I1 I2I2
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spectroscopy instruments FTIR (fourier transform infrered spectroscopy) fixed mirror moving mirror beam splitter detector
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FTIR spectrum
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spectroscopy instruments TDLS (tuneable diode laser spectroscopy)
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space instruments nadir viewlimb view (solar) occultation
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GOME and SCIAMACHY
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space borne DOAS courtesy T. Wagner, IUP Heidelberg
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Pixel resolution of tropospheric satellite measurements GOME SCIA OMI 1996-2003 2002- 2005- courtesy T. Wagner, IUP Heidelberg
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Dependence of GOME measurements on zenith angle and surface albedo courtesy T. Wagner, IUP Heidelberg
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Tropospheric NO 2 retrieval from GOME courtesy T. Wagner, IUP Heidelberg
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Tropospheric NO 2 retrieval from GOME courtesy T. Wagner, IUP Heidelberg
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Weekly NO 2 cycle courtesy S. Beirle, IUP Heidelberg
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distinction between uncertainty (aka „accuracy“) and random error (aka „precision“) calibration bias digitization noise, counting statistics error propagation Measurement uncertainty
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Uncertainty and random error measured distributiontrue value bias precision
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Calibration bias Frequent sources of error: offset problems uncertainty of reference value non-linearity of response curve conditions differing from ambient measurement instrument drift (e.g. temperature shifts)
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Counting statistics Several instruments detect their signal by counting photons (e.g. chemoluminescence detector). Obviously, the precision of such a measurement becomes better if the number of photons (the statistical sample) increases. The population standard deviation is given by: One effect of this is the lower limit of detection (LOD) achieved by averaging signals over longer time scales.
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Error Propagation To keep it simple:
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Bibliography Material for this lecture comes mostly from Brasseur, G.P., Orlando, J.J., and Tyndall, G.S., Atmospheric Chemkistry and Global Change, Oxford University Press, Oxford, New York, 1999. Finnlayson-Pitts and Pitts, 1986. Chemical ozone cell description from http://www.fz-juelich.de/icg/icg-ii/josie/ozone_sondes/ Error analysis: NCAR Advanced study programme course 1992 http://www.asp.ucar.edu/colloquium/1992/notes /
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