Publication
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Type of publication
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Peer-reviewed
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Publikationsform
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Original article (peer-reviewed)
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Author
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Hörtnagl Lukas,
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Project
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ICOS-CH Phase 2
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Show all
Original article (peer-reviewed)
Journal
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Journal of Open Source Software
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Volume (Issue)
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6(62)
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Page(s)
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2575 - 2575
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Title of proceedings
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Journal of Open Source Software
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DOI
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10.21105/joss
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Open Access
Abstract
In ecosystem research, the eddy covariance (EC) method is widely used to quantify the
biosphere-atmosphere exchange of greenhouse gases (GHGs) and energy (Aubinet et al., 2012;
Baldocchi et al., 1988). The raw ecosystem flux (i.e., net exchange) is calculated by the covariance
between the turbulent vertical wind component measured by a sonic anemometer
and the entity of interest, e.g., CO2, measured by a gas analyzer. Due to the application of
two different instruments, wind and gas are not recorded at exactly the same time, resulting
in a time lag between the two time series. For the calculation of ecosystem fluxes this time
delay has to be quantified and corrected for, otherwise fluxes are systematically biased. Time
lags for each averaging interval can be estimated by finding the maximum absolute covariance
between the two turbulent time series at different time steps in a pre-defined time window
of physically possible time-lags (e.g., McMillen, 1988; Moncrieff et al., 1997). Lag detection
works well when processing fluxes for compounds with high signal-to-noise ratio (SNR), which
is typically the case for e.g. CO2. In contrast, for compounds with low SNR (e.g., N2O, CH4)
the cross-covariance function with the turbulent wind component yields noisier results and
calculated fluxes are biased towards larger absolute flux values (Langford et al., 2015), which
in turn renders the accurate calculation of yearly ecosystem GHG budgets more difficult and
results may be inaccurate.
One method to adequately calculate fluxes for compounds with low SNR is to first calculate
the time lag for a reference compound with high SNR (e.g., CO2) and then to apply the
same time lag to the target compound of interest (e.g., N2O), with both compounds being
recorded by the same analyzer (Nemitz et al., 2018). DYCO uses this method by facilitating
the dynamic lag-detection between the turbulent wind data and a reference compound and
the subsequent application of found reference time lags to one or more target compounds.
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