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  • 1
    Online Resource
    Online Resource
    Dordrecht :Springer Netherlands,
    Keywords: Turbulent diffusion (Meteorology)--Measurement. ; Analysis of covariance. ; Eddy correlation. ; Micrometeorology. ; Atmosphärische Turbulenz. swd. ; Electronic books.
    Description / Table of Contents: This handbook provides exhaustive treatment of eddy covariance measurement. The chapters cover measuring fluxes using eddy covariance techniques, from the tower installation and system dimensioning to data collection, correction and analysis.
    Type of Medium: Online Resource
    Pages: 1 online resource (451 pages)
    Edition: 1st ed.
    ISBN: 9789400723511
    Series Statement: Springer Atmospheric Sciences Series
    DDC: 551.51
    Language: English
    Note: Intro -- Eddy Covariance -- Preface -- Contents -- Contributors -- Chapter 1: The Eddy Covariance Method -- 1.1 History -- 1.2 Preliminaries -- 1.2.1 Context of Eddy Covariance Measurements -- 1.2.2 Reynolds Decomposition -- 1.2.3 Scalar Definition -- 1.3 One Point Conservation Equations -- 1.3.1 Dry Air Mass Conservation (Continuity) Equation -- 1.3.2 Momentum Conservation Equation -- 1.3.3 Scalar Conservation Equation -- 1.3.4 Enthalpy Equation -- 1.4 Integrated Relations -- 1.4.1 Dry Air Budget Equation -- 1.4.2 Scalar Budget Equation (Generalized Eddy Covariance Method) -- 1.5 Spectral Analysis -- 1.5.1 Spectral Analysis of Turbulence -- 1.5.2 Spectral Analysis of Atmospheric Turbulence -- 1.5.3 Sensor Filtering -- 1.5.4 Impacts of Measurement Height and Wind Velocity -- References -- Chapter 2: Measurement, Tower, and Site Design Considerations -- 2.1 Introduction -- 2.2 Tower Considerations -- 2.2.1 Theoretical Considerations for Tower Design -- 2.2.1.1 Diverse Ecosystems and Environments -- 2.2.1.2 Physical Effects on Surrounding Flows Due to the Presence of Tower Structure -- 2.2.1.3 Size of Horizontal Supporting Boom -- 2.2.1.4 Tower Deflection and Oscillations -- 2.2.1.5 Recirculation Zone at the Opening in a Tall Canopy -- 2.2.2 Tower Design and Science Requirements -- 2.2.2.1 Tower Location Requirements -- 2.2.2.2 Tower Structure Requirements -- 2.2.2.3 Tower Height Requirements -- 2.2.2.4 Tower Size Requirements -- 2.2.2.5 Instrument Orientation Requirements -- 2.2.2.6 Tower Installation and Site Impact Requirements -- 2.3 Sonic Anemometer -- 2.3.1 General Principles -- 2.3.2 Problems and Corrections -- 2.3.3 Requirements for Sonic Choice, Positioning, and Use -- 2.4 Eddy CO2/H2O Analyzer -- 2.4.1 General Description -- 2.4.2 Closed-Path System -- 2.4.2.1 Absolute and Differential Mode. , 2.4.2.2 Tubing Requirements for Closed-Path Sensors -- 2.4.2.3 Calibration for CO2 -- 2.4.2.4 Water Vapor Calibration -- 2.4.3 Open-Path Systems -- 2.4.3.1 Installation and Maintenance -- 2.4.3.2 Calibration -- 2.4.4 Open and Closed Path Advantages and Disadvantages -- 2.4.5 Narrow-Band Spectroscopic CO2 Sensors -- 2.5 Profile Measurement -- 2.5.1 Requirements for Measurement Levels -- 2.5.2 Requirements for Profile Mixing Ratio Measurement -- References -- Chapter 3: Data Acquisition and Flux Calculations -- 3.1 Data Transfer and Acquisition -- 3.2 Flux Calculation from Raw Data -- 3.2.1 Signal Transformation in Meteorological Units -- 3.2.1.1 Wind Components and Speed of Sound from the Sonic Anemometer -- 3.2.1.2 Concentration from a Gas Analyzer -- 3.2.2 Quality Control of Raw Data -- 3.2.3 Variance and Covariance Computation -- 3.2.3.1 Mean and Fluctuation Computations -- 3.2.3.2 Time Lag Determination -- 3.2.4 Coordinate Rotation -- 3.2.4.1 Requirements for the Choice of the Coordinate Frame and Its Orientation -- 3.2.4.2 Coordinate Transformation Equations -- 3.2.4.3 Determination of Rotation Angles -- 3.3 Flux Determination -- 3.3.1 Momentum Flux -- 3.3.2 Buoyancy Flux and Sensible Heat Flux -- 3.3.3 Latent Heat Flux and Other Trace Gas Fluxes -- 3.3.4 Derivation of Additional Parameters -- References -- Chapter 4: Corrections and Data Quality Control -- 4.1 Flux Data Correction -- 4.1.1 Corrections Already Included into the Raw Data Analysis (Chap. 3) -- 4.1.2 Conversion of Buoyancy Flux to Sensible Heat Flux (SND-correction) -- 4.1.3 Spectral Corrections -- 4.1.3.1 Introduction -- 4.1.3.2 High-Frequency Loss Corrections -- 4.1.3.3 Low-Cut Frequency -- 4.1.4 WPL Corrections -- 4.1.4.1 Introduction -- 4.1.4.2 Open-Path Systems -- 4.1.4.3 WPL and Imperfect Instrumentation -- 4.1.4.4 Closed-Path Systems -- 4.1.5 Sensor-Specific Corrections. , 4.1.5.1 Flow Distortion Correction of Sonic Anemometers -- 4.1.5.2 Correction Due to Sensor Head Heating of the Open-Path Gas Analyzer LiCor 7500 -- 4.1.5.3 Corrections to the Krypton Hygrometer KH20 -- 4.1.5.4 Corrections for CH4 and N2O Analyzers -- 4.1.6 Nonrecommended Corrections -- 4.1.7 Overall Data Corrections -- 4.2 Effect of the Unclosed Energy Balance -- 4.2.1 Reasons for the Unclosed Energy Balance -- 4.2.2 Correction of the Unclosed Energy Balance -- 4.3 Data Quality Analysis -- 4.3.1 Quality Control of Eddy Covariance Measurements -- 4.3.2 Tests on Fulfilment of Theoretical Requirements -- 4.3.2.1 Steady State Tests -- 4.3.2.2 Test on Developed Turbulent Conditions -- 4.3.3 Overall Quality Flag System -- 4.4 Accuracy of Turbulent Fluxes After Correction and Quality Control -- 4.5 Overview of Available Correction Software -- References -- Chapter 5: Nighttime Flux Correction -- 5.1 Introduction -- 5.1.1 History -- 5.1.2 Signs Substantiating the Night Flux Error -- 5.1.2.1 Comparison with Bottom Up Approaches -- 5.1.2.2 Sensitivity of Flux to Friction Velocity -- 5.1.3 The Causes of the Problem -- 5.2 Is This Problem Really Important? -- 5.2.1 In Which Case Should the Night Flux Error Be Corrected? -- 5.2.2 What Is the Role of Storage in This Error? -- 5.2.3 What Is the Impact of Night Flux Error on Long-Term Carbon Sequestration Estimates? -- 5.2.4 What Is the Impact of the Night Flux Error on Functional Relationships? -- 5.2.5 What Is the Impact of the Night Flux Error on Other Fluxes? -- 5.3 How to Implement the Filtering Procedure? -- 5.3.1 General Principle -- 5.3.2 Choice of the Selection Criterion -- 5.3.3 Filtering Implementation -- 5.3.4 Evaluation -- 5.4 Correction Procedures -- 5.4.1 Filtering=+Gap Filling -- 5.4.2 The ACMB Procedure -- 5.4.2.1 History -- 5.4.2.2 Procedure -- 5.4.2.3 Evaluation -- References. , Chapter 6: Data Gap Filling -- 6.1 Introduction -- 6.2 Gap Filling: Why and When Is It Needed? -- 6.3 Gap-Filling Methods -- 6.3.1 Meteorological Data Gap Filling -- 6.3.2 General Rules and Strategies (Long Gaps) -- 6.3.2.1 Sites with Management and Disturbances -- 6.3.3 Methods Description -- 6.3.3.1 Mean Diurnal Variation -- 6.3.3.2 Look-Up Tables -- 6.3.3.3 Artificial Neural Networks -- 6.3.3.4 Nonlinear Regressions -- 6.3.3.5 Process Models -- 6.4 Uncertainty and Quality Flags -- 6.5 Final Remarks -- References -- Chapter 7: Uncertainty Quantification -- 7.1 Introduction -- 7.1.1 Definitions -- 7.1.2 Types of Errors -- 7.1.3 Characterizing Uncertainty -- 7.1.4 Objectives -- 7.2 Random Errors in Flux Measurements -- 7.2.1 Turbulence Sampling Error -- 7.2.2 Instrument Errors -- 7.2.3 Footprint Variability -- 7.2.4 Quantifying the Total Random Uncertainty -- 7.2.5 Overall Patterns of the Random Uncertainty -- 7.2.6 Random Uncertainties at Longer Time Scales -- 7.3 Systematic Errors in Flux Measurements -- 7.3.1 Systematic Errors Resulting from Unmet Assumptions and Methodological Challenges -- 7.3.2 Systematic Errors Resulting from Instrument Calibration and Design -- 7.3.2.1 Calibration Uncertainties -- 7.3.2.2 Spikes -- 7.3.2.3 Sonic Anemometer Errors -- 7.3.2.4 Infrared Gas Analyzer Errors -- 7.3.2.5 High-Frequency Losses -- 7.3.2.6 Density Fluctuations -- 7.3.2.7 Instrument Surface Heat Exchange -- 7.3.3 Systematic Errors Associated with Data Processing -- 7.3.3.1 Detrending and High-Pass Filtering -- 7.3.3.2 Coordinate Rotation -- 7.3.3.3 Gap Filling -- 7.3.3.4 Flux Partitioning -- 7.4 Closing Ecosystem Carbon Budgets -- 7.5 Conclusion -- References -- Chapter 8: Footprint Analysis -- 8.1 Concept of Footprint -- 8.2 Footprint Models for Atmospheric Boundary Layer -- 8.2.1 Analytical Footprint Models -- 8.2.2 Lagrangian Stochastic Approach. , 8.2.3 Forward and Backward Approach by LS Models -- 8.2.4 Footprints for Atmospheric Boundary Layer -- 8.2.5 Large-Eddy Simulations for ABL -- 8.3 Footprint Models for High Vegetation -- 8.3.1 Footprints for Forest Canopy -- 8.3.2 Footprint Dependence on Sensor and Source Heights -- 8.3.3 Influence of Higher-Order Moments -- 8.4 Complicated Landscapes and Inhomogeneous Canopies -- 8.4.1 Closure Model Approach -- 8.4.2 Model Validation -- 8.4.3 Footprint Estimation by Closure Models -- 8.4.4 Footprints over Complex Terrain -- 8.4.5 Modeling over Urban Areas -- 8.5 Quality Assessment Using Footprint Models -- 8.5.1 Quality Assessment Methodology -- 8.5.2 Site Evaluation with Analytical and LS Footprint Models -- 8.5.3 Applicability and Limitations -- 8.6 Validation of Footprint Models -- References -- Chapter 9: Partitioning of Net Fluxes -- 9.1 Motivation -- 9.2 Definitions -- 9.3 Standard Methods -- 9.3.1 Overview -- 9.3.2 Nighttime Data-Based Methods -- 9.3.2.1 Model Formulation: Temperature - Measurements -- 9.3.2.2 Reco Model Formulation -- 9.3.2.3 Challenges: Additional Drivers of Respiration -- 9.3.2.4 Challenges: Photosynthesis - Respiration Coupling and Within-Ecosystem Transport -- 9.3.3 Daytime Data-Based Methods -- 9.3.3.1 Model Formulation: The NEE Light Response -- 9.3.3.2 Challenges: Additional Drivers and the FLUXNET Database Approach -- 9.3.3.3 Unresolved Issues and Future Work -- 9.4 Additional Considerations and New Approaches -- 9.4.1 Oscillatory Patterns -- 9.4.2 Model Parameterization -- 9.4.3 Flux Partitioning Using High-Frequency Data -- 9.4.4 Flux Partitioning Using Stable Isotopes -- 9.4.5 Chamber-Based Approaches -- 9.4.6 Partitioning Water Vapor Fluxes -- 9.5 Recommendations -- References -- Chapter 10: Disjunct Eddy Covariance Method -- 10.1 Introduction -- 10.2 Theory -- 10.2.1 Sample Interval -- 10.2.2 Response Time. , 10.2.3 Definition of DEC.
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  • 2
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    PANGAEA
    In:  Supplement to: Vuichard, Nicolas; Papale, Dario (2015): Filling the gaps in meteorological continuous data measured at FLUXNET sites with ERA-Interim reanalysis. Earth System Science Data, 7(2), 157-171, https://doi.org/10.5194/essd-7-157-2015
    Publication Date: 2023-01-13
    Description: (preliminary) Exchanges of carbon, water and energy between the land surface and the atmosphere are monitored by eddy covariance technique at the ecosystem level. Currently, the FLUXNET database contains more than 500 sites registered and up to 250 of them sharing data (Free Fair Use dataset). Many modelling groups use the FLUXNET dataset for evaluating ecosystem model's performances but it requires uninterrupted time series for the meteorological variables used as input. Because original in-situ data often contain gaps, from very short (few hours) up to relatively long (some months), we develop a new and robust method for filling the gaps in meteorological data measured at site level. Our approach has the benefit of making use of continuous data available globally (ERA-interim) and high temporal resolution spanning from 1989 to today. These data are however not measured at site level and for this reason a method to downscale and correct the ERA-interim data is needed. We apply this method on the level 4 data (L4) from the LaThuile collection, freely available after registration under a Fair-Use policy. The performances of the developed method vary across sites and are also function of the meteorological variable. On average overall sites, the bias correction leads to cancel from 10% to 36% of the initial mismatch between in-situ and ERA-interim data, depending of the meteorological variable considered. In comparison to the internal variability of the in-situ data, the root mean square error (RMSE) between the in-situ data and the un-biased ERA-I data remains relatively large (on average overall sites, from 27% to 76% of the standard deviation of in-situ data, depending of the meteorological variable considered). The performance of the method remains low for the Wind Speed field, in particular regarding its capacity to conserve a standard deviation similar to the one measured at FLUXNET stations.
    Keywords: File name; LATITUDE; LONGITUDE; Site; Time in hours; Uniform resource locator/link to file
    Type: Dataset
    Format: text/tab-separated-values, 612 data points
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  • 3
    ISSN: 1365-2486
    Source: Blackwell Publishing Journal Backfiles 1879-2005
    Topics: Biology , Energy, Environment Protection, Nuclear Power Engineering , Geography
    Notes: This paper discusses the advantages and disadvantages of the different methods that separate net ecosystem exchange (NEE) into its major components, gross ecosystem carbon uptake (GEP) and ecosystem respiration (Reco). In particular, we analyse the effect of the extrapolation of night-time values of ecosystem respiration into the daytime; this is usually done with a temperature response function that is derived from long-term data sets. For this analysis, we used 16 one-year-long data sets of carbon dioxide exchange measurements from European and US-American eddy covariance networks. These sites span from the boreal to Mediterranean climates, and include deciduous and evergreen forest, scrubland and crop ecosystems.We show that the temperature sensitivity of Reco, derived from long-term (annual) data sets, does not reflect the short-term temperature sensitivity that is effective when extrapolating from night- to daytime. Specifically, in summer active ecosystems the long-term temperature sensitivity exceeds the short-term sensitivity. Thus, in those ecosystems, the application of a long-term temperature sensitivity to the extrapolation of respiration from night to day leads to a systematic overestimation of ecosystem respiration from half-hourly to annual time-scales, which can reach 〉25% for an annual budget and which consequently affects estimates of GEP. Conversely, in summer passive (Mediterranean) ecosystems, the long-term temperature sensitivity is lower than the short-term temperature sensitivity resulting in underestimation of annual sums of respiration.We introduce a new generic algorithm that derives a short-term temperature sensitivity of Reco from eddy covariance data that applies this to the extrapolation from night- to daytime, and that further performs a filling of data gaps that exploits both, the covariance between fluxes and meteorological drivers and the temporal structure of the fluxes. While this algorithm should give less biased estimates of GEP and Reco, we discuss the remaining biases and recommend that eddy covariance measurements are still backed by ancillary flux measurements that can reduce the uncertainties inherent in the eddy covariance data.
    Type of Medium: Electronic Resource
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  • 4
    Electronic Resource
    Electronic Resource
    Oxford, UK : Blackwell Science Ltd
    Global change biology 9 (2003), S. 0 
    ISSN: 1365-2486
    Source: Blackwell Publishing Journal Backfiles 1879-2005
    Topics: Biology , Energy, Environment Protection, Nuclear Power Engineering , Geography
    Notes: Recently flux tower data have become available for a variety of ecosystems under different climatic and edaphic conditions. Although Flux tower data represent point measurements with a footprint of typically 1 km × 1 km they can be used to validate models and to spatialize biospheric fluxes at regional and continental scales. In this paper we present a study where biospheric flux data collected in the EUROFLUX project were used to train a neural network simulator to provide spatial (1 km × 1 km) and temporal (weekly) estimates of carbon fluxes of European forests at continental scale. The novelty of the approach is that flux data were used to constrain and parameterize the neural network structure using a limited number of input driving variables. The overall European carbon uptake from this analysis was 0.47 Gt C yr−1 with distinctive differences between boreal and temperate regions. The length of the growing season is longer in the south of Europe (about 32 weeks), compared with north and central Europe, which have a similar length-growing season (about 27 weeks). A peak in respiration was depicted in spring at continental scale as a coherent signal which parallel the construction respiration increase at the onset of the season as usually shown by leaf level measurements.
    Type of Medium: Electronic Resource
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  • 5
    Publication Date: 2024-02-07
    Description: Since 1750, land use change and fossil fuel combustion has led to a 46 % increase in the atmospheric carbon dioxide (CO2) concentrations, causing global warming with substantial societal consequences. The Paris Agreement aims to limiting global temperature increases to well below 2°C above pre-industrial levels. Increasing levels of CO2 and other greenhouse gases (GHGs), such as methane (CH4) and nitrous oxide (N2O), in the atmosphere are the primary cause of climate change. Approximately half of the carbon emissions to the atmosphere is sequestered by ocean and land sinks, leading to ocean acidification but also slowing the rate of global warming. However, there are significant uncertainties in the future global warming scenarios due to uncertainties in the size, nature and stability of these sinks. Quantifying and monitoring the size and timing of natural sinks and the impact of climate change on ecosystems are important information to guide policy-makers’ decisions and strategies on reductions in emissions. Continuous, long-term observations are required to quantify GHG emissions, sinks, and their impacts on Earth systems. The Integrated Carbon Observation System (ICOS) was designed as the European in situ observation and information system to support science and society in their efforts to mitigate climate change. It provides standardized and open data currently from over 140 measurement stations across 12 European countries. The stations observe GHG concentrations in the atmosphere and carbon and GHG fluxes between the atmosphere, land surface and the oceans. This article describes how ICOS fulfills its mission to harmonize these observations, ensure the related long-term financial commitments, provide easy access to well-documented and reproducible high-quality data and related protocols and tools for scientific studies, and deliver information and GHG-related products to stakeholders in society and policy.
    Type: Article , PeerReviewed
    Format: text
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  • 6
  • 7
    Publication Date: 2017-10-10
    Description: Networks of eddy-covariance (EC) towers such as AmeriFlux, ICOS and NEON are vital for providing the necessary distributed observations to address grand challenges in earth system and carbon cycle science. NEON, once fully operational with 47 tower sites, will represent the largest single-provider EC network globally. Its standardized observation and data processing suite is designed specifically for inter-site comparability and analysis of continental-scale ecological change, including rich contextual data such as airborne remote sensing and in-situ sampling bouts. First carbon cycle products become available in 2017, including data and software. These products strive to incorporate lessons-learned through collaborations with AmeriFlux, ICOS, LTER and others, to suggest novel systemic solutions, and to synergize ongoing research efforts across science communities. Here, we present an overview of the ongoing product release, alongside efforts to integrate and synergize with existing infrastructures, networks and communities. Near-real-time carbon cycle observations in “basic” and “expanded”, self-describing HDF5 formats become accessible from the NEON Data Portal, including an Application Program Interface. A pilot project is underway to investigate their subsequent ingest into the AmeriFlux processing pipeline, together with inclusion in FLUXNET globally harmonized data releases. Software for reproducible, extensible and portable data analysis and science operations management also becomes available. This includes the eddy4R family of R-packages underlying the carbon cycle data product generation, together with the ability to directly participate in open development via GitHub version control and Dockerhub image hosting. In addition, templates for science operations management include a web-based field maintenance application and a graphical user interface to simplify problem tracking and resolution along the entire data chain. We hope that this first release of NEON carbon cycle products can initiate further collaboration and synergies in challenge areas, and would appreciate input and discussion on continued development.
    Repository Name: EPIC Alfred Wegener Institut
    Type: Conference , notRev
    Format: application/pdf
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  • 8
    Publication Date: 2021-06-29
    Description: The FLUXNET2015 dataset provides ecosystem-scale data on CO2, water, and energy exchange between the biosphere and the atmosphere, and other meteorological and biological measurements, from 212 sites around the globe (over 1500 site-years, up to and including year 2014). These sites, independently managed and operated, voluntarily contributed their data to create global datasets. Data were quality controlled and processed using uniform methods, to improve consistency and intercomparability across sites. The dataset is already being used in a number of applications, including ecophysiology studies, remote sensing studies, and development of ecosystem and Earth system models. FLUXNET2015 includes derived-data products, such as gap-filled time series, ecosystem respiration and photosynthetic uptake estimates, estimation of uncertainties, and metadata about the measurements, presented for the first time in this paper. In addition, 206 of these sites are for the first time distributed under a Creative Commons (CC-BY 4.0) license. This paper details this enhanced dataset and the processing methods, now made available as open-source codes, making the dataset more accessible, transparent, and reproducible.
    Repository Name: EPIC Alfred Wegener Institut
    Type: Article , isiRev
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  • 9
    Publication Date: 2024-04-12
    Description: This paper presents a use-case conducted within the ENVRI FAIR project, examining challenges and opportunities in deploying FAIR-aligned (ensuring Findability, Accessibility, Interoperability and Reusability) scientific name-matching services across Environmental Research Infrastructures (RIs). Six services were tested using various name variations, revealing inconsistencies in match types, status reporting and handling of canonical forms and typos. These diversities pose challenges for RI data pipelines and interoperability. The paper underscores the importance of standardised tools, enhanced communication, training, collaboration and shared resources. Addressing these needs can facilitate more effective FAIR implementation within the ENVRI community and biodiversity research. This, in turn, will empower RIs to seamlessly integrate and leverage scientific names, unlocking the full potential of their data for research and policy implementation.
    Keywords: scientific names ; taxonomy ; biodiversity ; FAIR ; ENVRI
    Repository Name: National Museum of Natural History, Netherlands
    Type: info:eu-repo/semantics/article
    Format: application/pdf
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