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<strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong> und Arbeitsstelle Radiometrie<br />

Annual Research Report<br />

2005<br />

<strong>Ruprecht</strong>-<strong>Karls</strong>-<strong>Universität</strong> Heidelberg<br />

und<br />

Heidelberger Akademie der Wissenschaften


Professor Dr. Karl Otto Münnich<br />

(1. 1. 1925 – 26. 10. 2003)<br />

It has been more than 25 years since the last Annual Report on the scientific work in our<br />

<strong>Institut</strong>e. We, thus, want to take this opportunity to commemorate Karl Otto Münnich,<br />

the founding father and first Director of the <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong> (Environmental<br />

Physics), to whom we dedicate this report.<br />

Karl Otto Münnich was born and grew up in Heidelberg. He studied Physics at the<br />

University of Heidelberg and received his doctoral degree in 1957. During his PhD work<br />

he established the Radiocarbon Dating Laboratory in Heidelberg which later became<br />

part of the Heidelberger Akademie der Wissenschaften (Academy of Sciences). Karl<br />

Otto Münnich quickly realised the universal significance of the Radiocarbon method<br />

far beyond its application in archaeology. As one of the first topics, together with John<br />

C. Vogel, he pioneered the ground water dating method. Also during the 1950s and 60s<br />

Münnich became witness of the dramatic consequences of atmospheric nuclear weapon<br />

testing on radionuclide concentrations in the environment. He was among the first<br />

to utilise this “global tracer experiment” and study exchange processes between the<br />

important compartments of the climate system, therewith establishing the new research<br />

field of Environmental Physics. After a sabbatical in the US and a directorate at the<br />

Forschungszentrum Jülich, Karl Otto Münnich was appointed director of the newly<br />

founded <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong> (<strong>Institut</strong>e for Environmental Physics) in 1974. Here<br />

he demonstrated a unique combination of abstract thinking in terms of fundamental<br />

physics, experimental skills, and interdisciplinary insight. His excellent sense to extract<br />

the pivotal points of the often highly complex processes in nature permitted him to<br />

elaborate fundamental, but still simple solutions in a variety of fields. He was an<br />

excellent and adored teacher, colleague and friend to many of us. Karl Otto Münnich<br />

attracted a large number of students, and his work became well established world-wide<br />

with many of his alumni now teaching this discipline themselves.<br />

Today the various methods originally introduced by Karl Otto Münnich are applied to<br />

all major environmental subsystems, where physics plays the central role for process<br />

understanding. At the Heidelberg <strong>Institut</strong>e his pioneering ideas have been well implemented<br />

and are successfully pursued. The 2005 Scientific Report nicely illustrates how<br />

we endeavour to carry Karl Otto Münnich’s early visions into the future.


Contents<br />

1 Introduction/Overview of institute 9<br />

2 Atmosphere and Remote Sensing 11<br />

2.1 Tropospheric Research Group . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 15<br />

2.1.1 Halogen oxide and sulphur dioxide emission of volcanoes . . . . . . . . . . . . . 19<br />

2.1.2 Studies of Reactive Halogen Species (RHS) in the Marine and mid-Latitudinal<br />

Boundary Layer by Active Longpath Differential Optical Absorption Spectroscopy<br />

(DOAS) . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 20<br />

2.1.3 Improvement of the Detection Limit of Active-DOAS-Measurements by use of<br />

fibre coupled light source . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 21<br />

2.1.4 New Operational Software for Automatic DOAS Measurement and Analysis . . 22<br />

2.1.5 Ground based MAX-DOAS measurements . . . . . . . . . . . . . . . . . . . . . 23<br />

2.1.6 Imaging DOAS. Imaging of two-dimensional trace gas distributions . . . . . . . 24<br />

2.1.7 Multi Axis Differential Optical Absorption Spectroscopy (MAX-DOAS) of Trace<br />

Gas and Aerosol Distributions . . . . . . . . . . . . . . . . . . . . . . . . . . . 25<br />

2.1.8 The flying laboratory: DOAS on board the CARIBIC aircraft project . . . . . 26<br />

2.1.9 Heidelberg ground-based network . . . . . . . . . . . . . . . . . . . . . . . . . . 27<br />

2.1.10 Applicability of light-emitting diodes as light sources<br />

for active DOAS measurements . . . . . . . . . . . . . . . . . . . . . . . . . . . 28<br />

2.1.11 Active DOAS measurements of trace gases in the free troposphere . . . . . . . 29<br />

2.1.12 Long Term Observations of Urban Atmospheric Radical Chemistry<br />

(TURBAN) . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 30<br />

2.2 Stratospheric Ozone . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 35<br />

2.2.1 Investigation of Inorganic Stratospheric Bromine . . . . . . . . . . . . . . . . . 38<br />

2.2.2 Stratospheric photochemistry of ozone, nitrogen and chlorine species . . . . . . 39<br />

2.2.3 Photolytic lifetime of stratospheric N2O5 . . . . . . . . . . . . . . . . . . . . . 40<br />

2.2.4 Spectroscopic measurements of halogen oxides in the marine boundary layer in<br />

Alcântara/Brazil . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 41<br />

2.2.5 Ground-based direct Sun UV/vis spectroscopy in Timon/Northeastern Brazil:<br />

Comparison of tropospheric air mass pollution in the dry and wet season . . . 42<br />

2.3 Radiative Transfer . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 45<br />

2.3.1 Development and Application of a Versatile Balloon-Borne DOAS Instrument<br />

for Skylight Radiance and Atmospheric Trace Gas Profile Measurements . . . . 48<br />

2.3.2 Oxygen A-band measurements for solar photon path length distribution studies 49<br />

2.3.3 Absolutely calibrated solar irradiance measurements . . . . . . . . . . . . . . . 50<br />

2.3.4 Atmospheric detection of water dimers and their contribution to solar shortwave<br />

absorption . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 51<br />

2.4 DOAS Tomography Group . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 55<br />

2.4.1 Intercomparison of ambient in-situ Formaldehyde Measurements in urban Air . 58<br />

2.4.2 Trace gas distributions from long-path DOAS measurements . . . . . . . . . . 59<br />

2.4.3 Airborne measurements of the CH2O and NO2 distributions in the Po basin . 60<br />

2.4.4 Development of a Multibeam instrument for simultaneous measurements along<br />

multiple light paths . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 61<br />

2.4.5 An Indoor Test Campaign of the Tomography Long Path Differential Optical<br />

Absorption Spectroscopy (DOAS) Technique . . . . . . . . . . . . . . . . . . . 62<br />

2.4.6 2D and 3D tomographic LP-DOAS measurements of trace gas distributions in<br />

Heidelberg over an area of 4 ∗ 4 km 2 . . . . . . . . . . . . . . . . . . . . . . . . 63<br />

2.4.7 Two-dimensional measurement of motorway emission plumes . . . . . . . . . . 64<br />

5


6 CONTENTS<br />

2.4.8 Two dimensional concentration distributions of a NO2 Emission plume from a<br />

point source derived by Airborne DOAS Tomography . . . . . . . . . . . . . . 65<br />

2.4.9 Development of a computer tool for the inversion and optimization of airborne<br />

tomographic DOAS measurements (Tomolab2) . . . . . . . . . . . . . . . . . . 66<br />

2.5 Satellite Group . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 69<br />

2.5.1 Quantifying NOx from lightning using satellite data . . . . . . . . . . . . . . . 72<br />

2.5.2 Evaluation of global tropospheric NO2 from SCIAMACHY . . . . . . . . . . . 73<br />

2.5.3 Development of a radiative transfer model . . . . . . . . . . . . . . . . . . . . . 74<br />

2.5.4 Retrieval of methane from SCIAMACHY onboard ENVISAT . . . . . . . . . . 75<br />

2.5.5 Retrieval of carbon monoxide from SCIAMACHY onboard ENVISAT . . . . . 76<br />

2.5.6 Retrieval of cloud parameters using SCIAMACHY and GOME data . . . . . . 77<br />

2.5.7 Satellite validation using the airborne multi axis DOAS instrument . . . . . . . 78<br />

2.5.8 Analysis of global long-term tropospheric and stratospheric BrO from GOME<br />

measurements . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 79<br />

2.5.9 Enhanced SO2 Column Densities Observed Over South East Asian Region: Consequence<br />

of El Niño . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 80<br />

2.5.10 Retrieving vertical profiles of stratospheric trace gases from satellite observations 81<br />

2.5.11 Comparison of OClO nadir measurements from SCIAMACHY and GOME . . 82<br />

2.5.12 Identification of tropospheric emissions sources from satellite observations: Synergistic<br />

use of HCHO and NO2 trace gas measurements . . . . . . . . . . . . . 83<br />

2.5.13 Trace gas profile retrieval from SCIAMACHY limb measurements . . . . . . . 84<br />

2.5.14 Mie theory based characterization and modeling of atmospheric aerosols . . . . 85<br />

2.5.15 Satellite observations of the global water vapor distribution . . . . . . . . . . . 86<br />

2.5.16 Analysis of MAXDOAS observations in various observing geometries . . . . . . 87<br />

2.5.17 Comparison of Radiative Transfer Models . . . . . . . . . . . . . . . . . . . . . 88<br />

2.5.18 GOME observations of stratospheric trace gas distributions during the split<br />

vortex event in the Antarctic winter 2002 . . . . . . . . . . . . . . . . . . . . . 89<br />

2.5.19 Comparison of GOME NO2 retrievals analysed by different scientific groups . . 90<br />

2.6 MarHal - Modeling of marine and halogen chemistry . . . . . . . . . . . . . . . . . . . 95<br />

2.6.1 Modeling the possible role of iodine oxides in new particle formation . . . . . . 99<br />

2.6.2 Ozone Depletion Events in the Polar Boundary Layer in Spring: A Model Study 100<br />

2.6.3 Modeling Organic Films on Atmospheric Aerosol Particles and their Influence<br />

on Cloud Microphysics and Chemistry . . . . . . . . . . . . . . . . . . . . . . . 101<br />

2.6.4 Impact of reactive bromine chemistry in the troposphere . . . . . . . . . . . . . 102<br />

2.7 Carbon Cycle Group . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 105<br />

2.7.1 Global long-term observations of Radiocarbon in atmospheric CO2, revisited . 108<br />

2.7.2 Simulating Bomb Radiocarbon: Implications for the Global Carbon Cycle . . . 109<br />

2.7.3 Coupling and modernisation of the Heidelberg Greenhouse Gases and CO - GC<br />

systems for continuous measurements . . . . . . . . . . . . . . . . . . . . . . . 110<br />

2.7.4 Investigating CO2, CO and Fossil Fuel CO2 in Heidelberg . . . . . . . . . . . . 111<br />

3 Terrestrial Systems 115<br />

3.1 Soil Physics . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 117<br />

3.1.1 Estimation of effective hydraulic parameters for heterogeneous porous media . 122<br />

3.1.2 X-ray attenuation techniques to study the dynamics of water in porous media . 123<br />

3.1.3 Fingered Flow Through Initially Dry Porous Hele-Shaw cell . . . . . . . . . . . 124<br />

3.1.4 Near Infrared Imaging Spectroscopy of Water States in Porous Silicate Media . 125<br />

3.1.5 Evaporation Experiment to determine Soil Hydraulic Properties . . . . . . . . 126<br />

3.1.6 Free Parameterisation of Soil Hydraulic Properties . . . . . . . . . . . . . . . . 127<br />

3.1.7 Modelling water flow and solute transport in heterogeneous soil . . . . . . . . . 128<br />

3.1.8 Unsaturated Flow in Strongly Heterogeneous Porous Media . . . . . . . . . . . 129<br />

3.1.9 Assessing temporal changes in volumetric soil water content from ground-penetrating<br />

radar profiles . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 130<br />

3.1.10 Monitoring Field Tracer Experiment with Ground Penetrating Radar and Time<br />

Domain Reflectometry . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 131<br />

3.1.11 Efficient reconstruction of dispersive dielectric profiles using TDR . . . . . . . 132<br />

3.1.12 3D Full-wave, electromagnetic model of ground penetrating radar systems . . . 133<br />

3.1.13 Simulation and Observation of an Evanescent Wave in Ground Penetrating<br />

Radar Applications . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 134<br />

3.2 Ice and Climate . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 137


CONTENTS 7<br />

3.2.1 Glaciological pilot studies on a cold miniature ice cap . . . . . . . . . . . . . . 140<br />

3.2.2 Constraining the anthropogenic fraction of carbonaceous aerosol by 14 C-analysis 141<br />

3.2.3 Recent variability of the cosmogenic nuclides 10 Be and 7 Be in coastal Antarctica 142<br />

3.2.4 Climatic significance of stable water isotope records from Alpine ice cores. . . 143<br />

3.2.5 Analyses of dissolved organic carbon (DOC) at low levels in Alpine and polar<br />

glaciers . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 144<br />

3.2.6 Novel tools in ice core research . . . . . . . . . . . . . . . . . . . . . . . . . . . 145<br />

4 Aquatic Systems 149<br />

4.1 Groundwater and Paleoclimate . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 151<br />

4.1.1 A tracer study of paleoclimate and groundwater recharge in the North China<br />

Plain . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 154<br />

4.1.2 A multi-tracer study of groundwater in reclamation areas south-west of the Nile<br />

Delta, Egypt . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 155<br />

4.1.3 A multi tracer study to investigate the groundwater in the Odenwald region . . 156<br />

4.1.4 A new mass spectrometric system for measurement of noble gases and first<br />

applications to perform measurements of fluid inclusions in speleothems . . . . 157<br />

4.1.5 Advancing the use of noble gases as palaeoclimate indicators . . . . . . . . . . 158<br />

4.1.6 Radon as tracer for lake - groundwater interaction . . . . . . . . . . . . . . . . 159<br />

4.2 Lake Research (Limnophysics) . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 161<br />

4.2.1 Sulfurhexaflourid (SF6) as tracer for transport and mixing processes in mining<br />

lakes . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 163<br />

4.2.2 Vertical transport in stratified lakes . . . . . . . . . . . . . . . . . . . . . . . . 164<br />

4.2.3 Investigation of Water Currents in Lake Willersinnweiher using Acoustic Doppler<br />

Current Profiler . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 165<br />

5 Small-Scale Air-Sea Interaction 167<br />

5.1 Small-Scale Air-Sea Interaction . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 169<br />

5.1.1 Investigation of transport processes across the sea-surface microlayer by active<br />

thermography . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 174<br />

5.1.2 Water flow measurements in environmental and biological systems . . . . . . . 175<br />

5.1.3 Time resolved Measurements of Air Water Gas Exchange . . . . . . . . . . . . 176<br />

5.1.4 3-D flow measurements within a porous gravel layer . . . . . . . . . . . . . . . 177<br />

5.1.5 3D fluid flow measurement close to surfaces . . . . . . . . . . . . . . . . . . . . 178<br />

5.1.6 Imaging concentration profiles of water boundary layer by Double-Dye LIF . . 179<br />

5.1.7 Combined slope/height measurements of short wind waves : ISHG . . . . . . . 180<br />

5.1.8 Development of a depth resolving boundary layer visualization for gas exchange<br />

at free water surfaces . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 181<br />

6 Forschungsstelle “Radiometrie” of the Heidelberger Akademie der Wissenschaften185<br />

6.1 Radiometric Dating of Water and Sediments . . . . . . . . . . . . . . . . . . . . . . . . 187<br />

6.1.1 Reconstruction of the geomagnetic field strength over the past 300,000 years<br />

derived from 10 Be data of deep sea sediments from the North and South Atlantic<br />

Ocean . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 191<br />

6.1.2 Possible solar origin of the glacial 1,470-year climate cycle demonstrated in a<br />

coupled climate model . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 192<br />

6.1.3 Solar variability and rapid climate change on decadal to centennial scales . . . 193<br />

6.1.4 Establishment of a method for measuring 231 Pa in deep-sea sediments via ICP-MS194<br />

6.1.5 Modelling of stable isotope records of stalagmites . . . . . . . . . . . . . . . . . 195<br />

6.1.6 Reconstruction of the 10 Be-production based on deep sea sediments from the<br />

North Atlantic . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 196<br />

6.1.7 U/Th dating of deep-water corals from the North Atlantic . . . . . . . . . . . . 197<br />

6.1.8 Isochron dating of fossil reef corals and the reconstruction of past sea level<br />

fluctuations . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 198<br />

6.1.9 Dating and interpretation of the carbon and oxygen isotopes of two Holocene<br />

stalagmites from the South of Chile (Patagonia) . . . . . . . . . . . . . . . . . 199<br />

6.1.10 Chronostratigraphy of the Nasca culture and palaeoclimate reconstruction of<br />

the Palpa region (Peru) by AMS- 14 C dating . . . . . . . . . . . . . . . . . . . . 200<br />

6.1.11 Nonlinear time-series analysis of nonstationary signals . . . . . . . . . . . . . . 201<br />

6.1.12 The authigenic 10 Be/ 9 Be ratio in deep sea sediments as a proxy for the Earth‘s<br />

magnetic field intensity . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 202


8 CONTENTS<br />

Bibliography 207<br />

Peer Reviewed Publications . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 209<br />

Grey Publications . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 215<br />

PhD Theses . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 217<br />

Diploma Theses . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 219<br />

Invited Talks . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 221


Introduction<br />

In Heidelberg, environmental physics continuously developed since the 1950s from the application of<br />

nuclear physics methods to environmental research, mainly driven by Otto Haxel. In 1975, this led to<br />

the foundation of the <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong> (<strong>Institut</strong>e of Environmental Physics), the first of its<br />

kind in Germany, in the Fakultät <strong>für</strong> Physik und Astronomie with Karl-Otto Münnich as its founding<br />

director.<br />

From the start, the IUP focused on the underlying physics of a wide spectrum of environmental processes<br />

and less on specific applications in atmospheric sciences, soil sciences, hydrology, or oceanography.<br />

This turned out to be a major strength and it continues to distinguish the IUP from other large<br />

environmental research institutes. With this focus, the IUP attains great flexibility in its methods<br />

and is able to provide an environment where classical divisions between systems and disciplines can<br />

be overcome. For instance, we investigate boundary layers between compartments which determine<br />

the soil-atmosphere and ocean-atmosphere interactions. This direction of research is also adopted<br />

by large international programs, like the International Geosphere Biosphere Project (IGBP), which<br />

in recent times focus increasingly on investigation of interaction between compartments of the Earth<br />

system. With its firm rooting in physics, the IUP sees itself in an excellent position to recognize and<br />

investigate system properties of our environment and the interplay of its subsystems (atmosphere,<br />

cryosphere, soil, groundwater, oceans,. . . ).<br />

The IUP is a strongly experiment-oriented institution. Our current major fields of research are:<br />

• physical foundations of climate research (budgets of greenhouse gases, oxidation capacity of the<br />

atmosphere, radiation in the atmosphere),<br />

• consequences of global change on central cycles in the earth system (water, carbon), and<br />

• reconstruction of paleoclimate from a variety of environmental archives.<br />

Our spectrum of methods still contains those developed from nuclear physics inheritance, specifically<br />

the analysis of 14 C and various stable isotopes including noble gases. In addition, we employ an<br />

array of new techniques like spectroscopy (of the atmosphere) and imaging spectroscopy, remote<br />

sensing from ground-, air-, and space-borne platforms, time series analysis, as well as experiment- and<br />

process-oriented modeling and simulation.<br />

This report gives a snapshot of the research performed at the IUP by diploma students, doctoral<br />

students, and senior scientist. It is intended as a comprehensive but concise overview for the members<br />

of the institute as well as for the scientific community.<br />

9


Atmosphere and Remote Sensing<br />

2.1 Tropospheric Research Group . . . . . . . . . . . . . . . . . . . . . . . . . 15<br />

2.2 Stratospheric Ozone . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 35<br />

2.3 Radiative Transfer . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 45<br />

2.4 DOAS Tomography Group . . . . . . . . . . . . . . . . . . . . . . . . . . . 55<br />

2.5 Satellite Group . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 69<br />

2.6 MarHal - Modeling of marine and halogen chemistry . . . . . . . . . . . 95<br />

2.7 Carbon Cycle Group . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 105<br />

11


Overview<br />

Summary<br />

Atmospheric research at the IUP concentrates on the processes governing the oxidation capacity<br />

of the atmosphere, its physical and chemical properties and its role in the global climate system.<br />

Central topics are release processes and the influence of reactive halogen species as well as other free<br />

radical cycles in the stratosphere and troposphere, fundamental research related to scattering and<br />

absorption of short-wave radiation transport in the atmosphere, and on the abundance and role of<br />

trace and greenhouse gases in atmospheric chemistry and in the climate system. Tools of our research<br />

are observing systems on global, continental and regional scales relying on sophisticated ground and<br />

aircraft-based in-situ and sampling techniques as well as air-borne and space-borne remote sensing.<br />

Observations are integrated in modeling studies of marine and stratospheric photochemistry with a<br />

particular focus put on the chemistry of halogens, atmospheric radiation transport, and on global,<br />

regional and trajectory models of source and sink processes of greenhouse gases.<br />

Central topics include:<br />

• Atmospheric composition and links to human health<br />

• Radiation transfer processes and links to climate<br />

• Tropospheric halogen species and their role in the oxidation capacity of the atmosphere<br />

• Stratospheric ozone as influenced by halogen and nitrogen species<br />

• Sources and sink processes as well as isotopic abundances of greenhouse gases<br />

• Global observing systems<br />

For a detailed description of the different topics see individual group reports.<br />

Atmospheric composition and links to human health<br />

Studies of radical processes in tropospheric chemistry were performed, free radicals determine the<br />

oxidation capacity of the troposphere, i.e. the capacity of the atmosphere to clean itself from natural<br />

and anthropogenic pollutants. Scientific objectives include studies of the processes governing the<br />

oxidation capacity of the troposphere. In particular the release and activation processes of reactive<br />

halogen species in the troposphere. Studies in this year centered on the following questions:<br />

• The abundance of reactive halogen species (BrO, IO, I2) in the marine boundary layer in coastal<br />

regions.<br />

• The abundance of reactive halogen species (BrO, IO) and related compounds over the open<br />

ocean.<br />

• The abundance of reactive halogen species, in particular BrO, and related species like NO2, NO3<br />

and CH2O in the free troposphere<br />

• The rate of volcanic emissions of reactive halogen species, e.g. BrO, ClO, OClO.<br />

• Chemical evolution of reactive halogen species in volcanic plumes, in particular what are the<br />

processes after O2 and O3 mixes into the originally reducing plume.<br />

For a detailed description of the different topics see individual group reports.<br />

Future Work<br />

Future work will encompass<br />

1. Establishment of a large network of ground based remote sensing instruments to quantify volcanic<br />

emissions, which will provide the first comprehensive study of volcanic sulfur and halogen<br />

emissions (EU-project NOVAC).<br />

2. Study of the marine halogen chemistry with particular emphasis on iodine-particle formation<br />

(EU-project MAP), nonlinear chemistry, and emission ”hot spots”.<br />

13


14 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

3. Spectroscopic studies of atmospheric particles will be performed within a large long-term intercomparison<br />

exercise (EU-project ICARTT).<br />

4. Study of the inter-annual variation of the solar radiation field including 2-D imaging spectroscopy<br />

of the radiative properties of the atmosphere with a particular focus on the radiative properties<br />

during the life cycle of individual clouds (DFG Forschergruppe ’life cycles of clouds’)<br />

5. Using novel ballon-based instrumentation (Mini-DOAS), the time-dependence of ozone destroying<br />

radicals (BrO, and OClO) and inferred reactive chlorine will be investigated from which<br />

conclusions on the most important loss reactions for stratospheric ozone in polar winter can be<br />

drawn.<br />

6. Investigation of the transport and photochemical processes at the major entrance of tropospheric<br />

air into the stratosphere, i.e. the tropical upper troposphere layer/lowermost stratosphere<br />

(TTL/LMS) Conclusions will be drawn on the ozone depletion potential of major manmade<br />

and naturally emitted ozone destroying chemicals passing the TTL/LMS (EU-project<br />

SCOUT-O3).<br />

7. Study of the European carbon balance and in particular the fossil fuel CO2 contribution (EUproject<br />

CarboEurope-IP)<br />

8. Within the carbon system, investigation of independent constraints on global carbon exchange<br />

as derived from long-term high precision 14 CO2 observations in combination with model studies<br />

(DFG project, Atmospheric 14 C).<br />

9. Investigation of the continental European hydrogen budget (in particular the anthropogenic<br />

source and the soil sink) using continuous and aircraft observations over Europe and Siberia<br />

(EUROHYDROS and TCOS II, submitted EU proposals)<br />

Instrument development will be continued, a particular topic being preparation for the new German<br />

research aircraft HALO. In this context we are developing novel instruments based on imaging and<br />

near-IR spectroscopy.<br />

Literature<br />

A total of 16 peer reviewed manuscripts where accepted by or appeared in scientific journals. Members<br />

of the institute were invited to give 19 presentations on topics related to atmospheric research at<br />

scientific conferences<br />

Diploma and Doctoral Theses<br />

A total of 4 Diploma theses and 2 Doctoral theses on topics related to atmospheric research were<br />

completed in the reporting period.


2.1. TROPOSPHERIC RESEARCH GROUP 15<br />

2.1 Tropospheric Research Group<br />

Group members<br />

Prof Dr. U. Platt, Chief of Staff<br />

Dipl. Phys. N. Bobrowski, PhD Student<br />

Dipl. Phys. B. Dix, PhD Student<br />

M. Gillmann, Staff<br />

MSc. O. Ibrahim, PhD Student<br />

Dipl. Phys. C. Kern, PhD Student<br />

I. Louban, Diploma Student<br />

Dipl. Phys. A. Merten, PhD Student<br />

Dr. C. Peters, Post Doc<br />

K. Seitz, Diploma Student<br />

Dipl Phys. R. Sinreich, PhD Student<br />

T. Stein, Diploma Student<br />

Dr. S. Trick, Staff<br />

Dr. J. Zingler, Post Doc<br />

Abstract<br />

Tropospheric research in the IUP concentrates on the processes governing the oxidation capacity of the<br />

atmosphere. Of particular interest are release processes of reactive halogen species from a multitude of<br />

sources (marine biology, sea spray, volcanoes, etc.) into the troposphere. Consequences for the state<br />

of the troposphere are studied together with the other atmospheric subgroups and within national<br />

and international collaborations.<br />

Scientific Objectives<br />

include studies of the processes governing the oxidation capacity of the troposphere. In particular the<br />

release and activation processes of reactive halogen species in the troposphere. the questions studied<br />

in this year centered on the following questions:<br />

• The abundance of reactive halogen species (BrO, IO, I2) in the marine boundary layer in coastal<br />

regions.<br />

• The abundance of reactive halogen species (BrO, IO) and related compounds over the open<br />

ocean.<br />

• The abundance of reactive halogen species, in particular BrO, and related species like NO2, NO3<br />

and CH2O in the free troposphere.<br />

• The rate of volcanic emissions of reactive halogen species, e.g. BrO, ClO, OClO.<br />

• Chemical evolution of reactive halogen species in volcanic plumes, in particular what are the<br />

processes after O2 and O3 mixes into the originally reducing plume.<br />

Overarching topic<br />

Studies of radical processes in tropospheric chemistry, the oxidation capacity of the troposphere, i.e.<br />

the camacity of the atmosphere to clean itself from natural and anthropogenic pollutants.<br />

Background<br />

Free radicals play a pivotal role in atmospheric chemistry. Despite their exceedingly small concentration<br />

(mixing ratios around 10-12), these species are the driving force for most chemical processes<br />

in the atmosphere. While the role of hydrogen radicals (OH, HO2) is relatively well studied and<br />

largely understood, other free radicals like halogen atoms or halogen oxides (e.g. IO, BrO, ClO) have<br />

been neglected until recently. In particular, at the levels suggested by the available measurements<br />

tropospheric halogen species can have profound effects on many aspects of tropospheric chemistry,<br />

these include: (1) Reactive halogen species, and in particular reactive bromine and iodine can readily<br />

destroy tropospheric ozone, which can have a multitude of consequences, both chemical and climatic<br />

(e.g. [Roscoe et al. , 2001], [Platt & Hönninger, 2003]). Catalytic ozone destruction essentially occurs<br />

by two distinct reaction cycles. Either (I) involving self reaction of halogen oxide radicals with other<br />

halogen oxide radicals (XO+XO or XO+YO) or (II) reaction of halogen oxides with hydrogen radicals


16 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

XO+HO2): leading to the net result:<br />

O3 + O3 → 3O2<br />

Cycle (I) has been identified as the prime cause for polar boundary layer ozone destruction [Barrie<br />

& Platt, 1997]. Since the rate of ozone destruction is usually proportional to the square of the halogen<br />

oxide concentration, cycle (I) ineffective at low XO levels usually found in mid-latitude coastal<br />

areas. At low RHS levels, however O3 destruction takes place by reaction cycle II, here the rate of<br />

O3 destruction is linearly dependent on the XO concentration. (2) An important side effect of cycle<br />

(II) the conversion of HO2 to OH and thus a reduction of the HO2/OH ratio, in particular at low<br />

NOX levels. At a given photochemical situation (O3, H2O levels, insolation) the presence of BrO or<br />

IO will therefore increase the OH concentration. It is interesting to note that both effects have been<br />

observed in the upper troposphere (e.g. [Wennberg et al. , 1998]). (3) The reaction of XO with NO,<br />

leads to conversion of NO to NO2 and thus to an increase of the Leighton ratio (L=[NO2]/[NO]). An<br />

increase in L is thus usually regarded as an indicator for photochemical ozone production (due to the<br />

presence of RO2 (R = organic radical)) in the troposphere. However, as already noted by [Platt &<br />

Janssen, 1996] an increase in L due to halogen oxides will not lead to O3 production. (4) A more<br />

subtle consequence of reactive halogen species for the ozone levels in the free troposphere is due to<br />

the combination of the above effects (2) and (3) as pointed out by [Stutz et al. , 1999]: Photochemical<br />

ozone production in the troposphere is limited by the reaction<br />

(2.1)<br />

NO + HO2 → NO2 + OH (2.2)<br />

However, the presence of reactive bromine will reduce the concentrations of both educts of the above<br />

reaction and thus reduce the NOX - catalysed ozone production. (5) Heterogeneous reactions of<br />

bromine species (i.e. HOBr) with (sea salt) chloride can lead to the release of Cl-atoms. This process<br />

constitutes a Br catalysed chlorine activation. Since Cl-atoms are highly reactive, this process directly<br />

enhances the oxidation capacity of the troposphere, see e.g. [Platt et al. , 2004]. (6) Gas-phase iodine<br />

species (like IO, OIO or HOI) may facilitate transport of I from the coast to inland areas and thus<br />

contribute to our iodine supply [Cauer, 2004], [Cox et al. , 1999]. (7) Deposition of mercury was found<br />

to be enhanced by the presence of reactive bromine species in particular in polar regions (e.g. [Barrie<br />

& Platt, 1997]), this process appears to be linked to the oxidation of Hg0 to Hg(II), likely by reaction<br />

with BrO [Lindberg et al. , 2002]. (8) The reaction of BrO with dimethyl sulfide (DMS) might be<br />

important in the unpolluted remote marine boundary layer where the only other sink for DMS is<br />

the reaction with OH radicals (e.g. [von Glasow et al. , 2004], [von Glasow & Crutzen, 2004]). (9)<br />

Iodine species have been shown to be involved in particle formation in the marine BL ([Leck & Bigg,<br />

1999], [Hoffmann et al. , 2001], [O’Dowd et al. , 2002], [Burkholder et al. , 2004]). (10) Evidence is<br />

accumulating (see e.g. [Platt & Hönninger, 2003]) that there is a wide-spread ”background” level of<br />

BrO radicals in the free troposphere, due to the processes described under (1)-(5) and (8) above there<br />

might be an important effect of reactive halogens on the global tropospheric chemistry as summarised<br />

by [von Glasow et al. , 2004].<br />

Main methods<br />

include the experimental determination of the halogen oxide distribution and the distribution of related<br />

species in several compartments of the troposphere: 1) The marine boundary layer in coastal regions<br />

(French Brittany). 2) The open ocean. 3) The free troposphere 4) Volcanic emissions (contents of<br />

reactive halogen species, e.g. BrO, ClO, OClO in volcanic plumes) The measurements are made by<br />

Differential Optical Absorption Spectroscopy (DOAS), which allows the detection of many atmospheric<br />

trace gases at a sensitivity in the ppt - range (i.e. at mixing ratios down to 10-12ppt). For studies<br />

in the different compartments a series of variants of the technique were applied: 1) Studies in the<br />

marine boundary layer were performed by active DOAS (i.e. using artificial light sources), which<br />

allows also nighttime studies, as well as by passive ”Multi-Axis” DOAS (MAX-DOAS). 2) Shipborne<br />

measurements in the open ocean relied on MAX-DOAS observations requiring relatively little<br />

logistic prerequisites and allowed unattended operation. 3) Aircraft-based measurements in the free<br />

troposphere are also based on passive MAX-DOAS observations, while ground based observations<br />

(at the Zugspitze) employ active DOAS measurements. 4) Observation at volcanoes were made by<br />

passive MAX-DOAS and by the novel Imaging-DOAS technique recently developed in our group. In<br />

addition to the field campaigns a number of projects is aimed at technological improvements of the<br />

DOAS technology. Activities included studies on the reduction of the optical noise [Platt, 1994] by the<br />

use of optical fibers and mode mixers to connect light source and transmitting telescope, the use of


2.1. TROPOSPHERIC RESEARCH GROUP 17<br />

Light Emitting Diodes as DOAS light sources, and development of novel techniques for the inversion<br />

of MAX-DOAS measurements to derive the aerosol optical density as well as the vertical distribution<br />

of trace gases in the lower atmosphere.<br />

Main activities<br />

A large number of field campaigns were conducted:<br />

• Expeditions to the volcanoes Etna (Italy) and ... to study emission of halogen oxide radicals<br />

and SO2.<br />

• Studies of nitrate radicals and related species at the Schneeferner Haus (Zugspitze, Germany)<br />

• Ship expedition (on RV Polarstern) during ... to study the NO2, O3, and BrO from 52 o S to<br />

72 o N.<br />

• Studies of the oxidation capacity of the lower atmosphere in New England (USA ) within the<br />

framework of the ICARTT project.<br />

• Participation in the CARIBIC - Project.<br />

• Also world wide long-term measurements of halogen oxides and related species were performed<br />

by the ”Heidelberg Ground-Based Network”.<br />

Funding<br />

DORSIVA (EU)<br />

IALSI (EU)<br />

AFO-2000: ReHaTrop (BMBF)<br />

CARIBIC<br />

Two Ph.D. students are funded through the International Max-Planck Research School in ”Experimental<br />

Atmospheric Chemistry”<br />

Cooperation within the institute and with groups outside of the institute<br />

Obviously there is close cooperation within the atmospheric groups.<br />

National and international cooperation exists with the following groups:<br />

Chalmers University, Gothenburg, Sweden (Galle)<br />

Volcanic observatory Etna, Italy<br />

Max-Planck Institue for Chemistry, Mainz<br />

University of Mainz (Heumann)<br />

University of Bayreuth<br />

<strong>Institut</strong>e for Physical Chemistry, University of Wuppertal (Barnes)<br />

Alfred Wegener <strong>Institut</strong>e for Polar Research, Bremerhafen<br />

NOAA, Boulder<br />

University of Cambridge (Oppenheimer)<br />

Future Work<br />

will encompass the establishment of a large network of volcanic stations to provide the first comprehensive<br />

and quantitative study of volcanic sulfur and halogen emissions (EU-project NOVAC). Also<br />

marine halogen chemistry will be studied, particular emphasis will be of iodine-particle formation (EUproject<br />

MAP), nonlinear chemistry, and emission ”hot spots”. Spectroscopic studies of atmospheric<br />

particles will be performed within a large long-term intercomparison exercise (EU-projcet ICARTT).<br />

Instrument development will be continued, a particular topic being preparation for the new German<br />

research aircraft HALO.<br />

Peer Reviewed Publications<br />

1. Sinreich et al. [2005]<br />

2. von Friedeburg et al. [2005]<br />

3. Pundt et al. [2005]


18 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

4. Zingler & Platt [2005]<br />

5. Volkamer et al. [2005]<br />

6. Bobrowski et al. [2005]<br />

7. Tas et al. [2005]<br />

8. Wenig et al. [2005]<br />

9. Hak et al. [2005]<br />

10. Peters et al. [2005]<br />

11. Kern et al. [2005]<br />

12. Lee et al. [2005]<br />

13. Wagner et al. [2004]<br />

14. Platt et al. [2004]<br />

15. von Glasow et al. [2004]<br />

Other Publications<br />

1. Platt et al. [2005]<br />

2. Volkamer et al. [2004]<br />

Diploma Theses<br />

1. Kern [2004]<br />

2. Louban [2005]<br />

3. Seitz [2005]<br />

PhD Theses<br />

1. Bobrowski [2005]<br />

2. Peters [2005]


2.1. TROPOSPHERIC RESEARCH GROUP 19<br />

2.1.1 Halogen oxide and sulphur dioxide emission of volcanoes<br />

Participating scientist Nicole Bobrowski<br />

Abstract A novel instrument, the ’Mini-MAX-DOAS’ was applied to study reactive halogen and<br />

sulphur emissions of several volcanoes. The study was focussed on the determination of SO2 and BrO<br />

concentrations, but also ClO and OClO could be detected for the first time in a volcanic plume. The<br />

chemistry of volcanic plumes can give insights into volcanic processes, which could help to improve the<br />

forecast of volcanic eruptions and is also of atmospheric relevance as the volcanic source of aerosols<br />

and trace gases can have significant climatic impact.<br />

Figure 2.1: The BrO/SO2 ratios for the different distances from the summit (left panel). Sketch of<br />

processes in a volcanic plume: after emission the plume mixes with ambient air, thus ozone becomes<br />

available and radical chemistry starts (right panel).<br />

Background The chemistry of volcanic plumes<br />

can give insights into volcanic processes, which<br />

could help improving the forecast of volcanic eruptions<br />

and is also of atmospheric relevance as the<br />

volcanic source of aerosols and trace gases can<br />

have a significant climatic impact. Although both<br />

are very important aspects until now the chemical<br />

processes are hardly understood and unfortunately<br />

still rarely studied.<br />

Funding IMPRS Fellowship and DORSIVA<br />

(Development of Optical Remote Sensing for Volcanic<br />

Applications- EU-project)<br />

Methods and results Spectroscopic measurements<br />

were carried out with the new Mini-MAX-<br />

DOAS instrument combined with a Pocket PC.<br />

The main results obtained in this work are: BrO<br />

is formed downwind, although it is not yet clear<br />

by what chemical processes. Nevertheless a suggested<br />

chemistry is given in Figure 1, right panel.<br />

Experimental studies at two volcanic sites, Mt.<br />

Etna and Mt. Villarica, were carried out and<br />

showed similar results. At Mt. Etna, measurements<br />

took place from the summit up to a distance<br />

of 19 km in downwind direction (see Figure 2.1,<br />

left panel). ClO and OClO were detected for the<br />

first time as further active halogen compounds in<br />

volcanic plumes. ClO was already detected next<br />

to the source (in contrast to BrO), and shows no<br />

significant increase in the ClO/SO2 ratio in the<br />

aging plume. The ClO/SO2 ratio even seems to<br />

decrease by measuring further downwind.<br />

The BrO/SO2 variations were studied during and<br />

after the Mt. Etna eruption 2004. They were<br />

compared with filter pack measurements and SO2<br />

flux variations. This measurements show differences<br />

of the feeding systems of Mt. Etna (North<br />

East Crater and Voragine). The North East<br />

Crater showed larger BrO/SO2 ratios than Voragine.<br />

Outlook/Future work The Mini-MAX-<br />

DOAS system will be set-up at many volcanic<br />

sites in the frame of a new started EU-project -<br />

NOVAC. The extension of the data set will open<br />

the possibility of a better estimation of the volcanic<br />

reactive bromine source and also allows the<br />

investigation of changes in the BrO/SO2 ratio<br />

with volcanic activity.<br />

Main publications [Bobrowski, 2005],<br />

[Bobrowski & Filsinger, 2005],<br />

[Bobrowski et al. , 2005]


20 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

2.1.2 Studies of Reactive Halogen Species (RHS) in the Marine and mid-<br />

Latitudinal Boundary Layer by Active Longpath Differential Optical<br />

Absorption Spectroscopy (DOAS)<br />

Participating scientist Christina Peters<br />

Abstract Appearance and distribution of a variety of reactive halogen species like BrO, IO, OIO<br />

and I2 in coastal areas was investigated within the framework of this PhD thesis.<br />

Figure 2.2: I2 time series recorded during the Mace Head campaign in 1998. The dotted line indicates<br />

the mean detection limit of 20 ppt. The shaded areas indicate I2 clearly identified above the detection<br />

limit (with respect to the individual error<br />

Background The importance of reactive halogen<br />

species (RHS) in the troposphere is on the one<br />

hand due to their strong effect on tropospheric<br />

ozone levels, which was discovered during ozone<br />

depletion events in the polar boundary layer during<br />

polar sunrise. On the other hand recent field<br />

and laboratory studies are indicating a great relevance<br />

of reactive iodine in new particle formation<br />

processes. Since particles in the marine atmosphere<br />

affect the microphysical properties of<br />

clouds, they have a potential impact on climate.<br />

Funding PhD Thesis in the framework of the<br />

AFO2000 program, funded by the BMBF.<br />

Methods and results Within the framework<br />

of this thesis three field campaigns using active<br />

longpath DOAS technique for studies of the<br />

reactive halogen species BrO, IO, OIO and I2<br />

were conducted in different mid-latitudinal regions.<br />

Ground based measurements in the lower<br />

Arctic at the Hudson Bay yielded high levels<br />

of the BrO radical up to 35 ppt in the boundary<br />

layer, coinciding with nearly complete surface<br />

near ozone depletion. Two field campaigns investigated<br />

the appearance of RHS in the coastal<br />

environments of the German North Sea and the<br />

French Atlantic Coast, IO was the only halogen<br />

oxide found in both locations with concentrations<br />

reaching 7.7±0.5 ppt. BrO in the marine boundary<br />

layer was estimated to remain below 1.5 ppt,<br />

neither OIO nor I2 could be unequivocally identified<br />

in the spectra. Within a re-analysis of spectra<br />

taken during an earlier campaign in 1998 in Mace<br />

Head, Ireland up to 61±12 ppt I2 were detected at<br />

night during extraordinary low water levels. Most<br />

likely the I2 was emitted by laminaria algae inhabiting<br />

parts of the lower intertidal zone.<br />

Outlook/Future work Further studies will be<br />

performed within the EU project ”Marine Aerosol<br />

Production” (MAP).<br />

Main publications [Peters et al. , 2005],<br />

[Peters, 2005]


2.1. TROPOSPHERIC RESEARCH GROUP 21<br />

2.1.3 Improvement of the Detection Limit of Active-DOAS-Measurements<br />

by use of fibre coupled light source<br />

Participating scientist André Merten<br />

Abstract Xenon-high-pressure lamps are commonly used in DOAS measurements. Unfortunately<br />

these lamps show strong spectral variability, which determines the minimum detectable optical density.<br />

A combination of a technical solution and a mathematical treatment to reduce the residual structures<br />

and therefore the detection limit was developed.<br />

Figure 2.3: Fibre light source prevents residual structures caused by a Xenon lamp.<br />

Background In active DOAS meausurements<br />

the minimum detectable optical density and thus<br />

the detection limit for trace gases are primarily<br />

determined by the spectral stability of the Xenonlight<br />

source. This is particularly important in<br />

spectral ranges where Xe-lines exist. Due to the<br />

large temperature gradient (several 1000 K/mm)<br />

and turbulent flow inside the arc these spectral<br />

structures strongly vary with time and across the<br />

arc of the Xe–high pressure lamp. When using<br />

a ’shortcut optics’, to remove this Xe-lines by<br />

a lamp reference, it is not guaranteed that the<br />

same area of the arc is imaged as is used in the<br />

measurement, causing strong residual structures<br />

which can be misinterpreted as optical densities.<br />

Imaging the lamp in a fibre and ’mode-mixing’ the<br />

light improves the situation, since all light leaving<br />

the fibre has the same spectral composition.<br />

Funding IALSI<br />

Methods and results After preliminary tests,<br />

a fibre coupled Xe-lamp was installed at the White<br />

cell (multireflection cell) at the EUPHORE smog<br />

chamberb (CEAM Valencia / Spain). Tests before<br />

and after the installation of this arrangement<br />

show a clear reduction of the residual structures<br />

and of the error in the concentration of detected<br />

trace gases. For a long path telescope it<br />

is even more complicated to run a short cut system<br />

that images the lamp arc in the same way<br />

as in the measurement mode, if the lamp is im-<br />

aged directly into the telescope. The Xenon-lamp<br />

was replaced by a Xenon-fibre light source, which<br />

was mounted at the optical axis of the telescope,<br />

instead of a Newton-like telescope set-up, which<br />

makes the complicate alignment of the telescope<br />

easier. Figure 2.3 shows the results of a DOAS<br />

evaluation of NO2 and H2O from the old (left)<br />

and the new (right) set-up. In the left graph<br />

strong residual structures dominate the fit-result.<br />

In the right graphs (new set-up with fibre source),<br />

only very small residual structures are visible and<br />

the detection of weak water absorption is possible.<br />

Due to the easier alignment, effectively no<br />

loss of light occurred. Xenon lamps show also a<br />

spectral drift with time. If it is not possible to<br />

take lamp spectra at short time periods, residual<br />

structures arise. Fortunately the spectrum of<br />

the lamp does not change randomly, which can be<br />

determined by correlation analysis of lamp spectra.<br />

A linear model can describe the variation of<br />

the lamp spectrum. This was combined with the<br />

DOAS-analysis. A change in the lamp spectrum is<br />

now treated like an absorber and can removed by<br />

the fitting procedure. The necessary mathematical<br />

functions were integrated in a new evaluation<br />

software, developed to perform an efficient DOAS<br />

analysis.<br />

Outlook/Future work Using fibre optics offers<br />

the possibility to work with other light sources<br />

such as LED and to design a new type of long path<br />

telescopes.


22 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

2.1.4 New Operational Software for Automatic DOAS Measurement and<br />

Analysis<br />

Participating scientist André Merten<br />

Abstract The opportunity offered by the DOAS method to do an automatic measurement and<br />

analysis of atmospheric trace gases has not been used because of the leak of adequate software. The<br />

requirements of modern measurement software were studied and a new, easier to handle DOASsoftware<br />

was developed, which can be used to monitor trace gases.<br />

Figure 2.4: Screen shots of the program ’LabDOAS Measurement’.<br />

Background The DOAS method is only practicable<br />

by use of computers. Therefore, the software<br />

is of great importance for the quality of measurement<br />

and data evaluation – especially for a fully<br />

automatic measurement and analysis mode e.g.<br />

for monitoring air quality. The DOAS method<br />

should be an analytical tool in atmospheric science,<br />

and instead the major content of the work.<br />

To meet this requirements, a new software tool<br />

was designed.<br />

Funding IALSI<br />

Methods and results The requirements for a<br />

modern DOAS software were determined:<br />

• Reliable communication with instrument<br />

controllers<br />

• Complete control by graphical user interface<br />

(GUI)<br />

• Status of the devices and the measurement<br />

is reported by graphs<br />

• Recording of all important information together<br />

with the spectra (digital log-book)<br />

• Parallel execution of measurement and data<br />

analysis<br />

• Automatic documentation of measurement<br />

and analysis (as text and graphics)<br />

According to these requirements a software package<br />

consisting of three programs based on Lab-<br />

VIEW was developed: The program ’LabDOAS<br />

MEASUREMENT’ controls an active DOAS device.<br />

It can run in an automatic measurement<br />

and evaluation mode, completely controlled by<br />

GUI and remote acces. Status of measurement<br />

and analysis are exported automatically as graphics.<br />

The easy handling supports the operator especially<br />

in case of adjusting the DOAS device.<br />

’LabDOAS ANALYSIS’ is designed for more intensive<br />

data evaluation. A single spectrum as<br />

well a whole time series of spectra can be analysed<br />

with mathematical functions like digital filters<br />

and Fourier transformation, including methods<br />

to analyse residual structures of lamp spectra<br />

like correlation analysis. ’LabDOAS CALIBRA-<br />

TION’ offers automatic wavelength calibration of<br />

the spectrograph with spectra of atomic emmissions.<br />

It contains a comprehensive database of<br />

atomic spectral lines. This calibration is used to<br />

prepare the reference cross sections for the DOAS<br />

evaluation.<br />

Outlook/Future work This software package<br />

was tested successfully at a long path telescope<br />

and has shown its advantages also in the examination<br />

of lamp noise and exploration of absorption<br />

cross sections. Additional functions such as<br />

automatic adjusting and evaluation of stray light<br />

spectra are in preparation.


2.1. TROPOSPHERIC RESEARCH GROUP 23<br />

2.1.5 Ground based MAX-DOAS measurements<br />

Participating scientists Ossama Ibrahim, Thomas Wagner, Ulrich Platt<br />

Abstract The Multi-axis DOAS technique uses scattered sunlight to obtain information about the<br />

trace gases in the atmosphere by pointing a telescope to different elevation angles and thus receiving<br />

light from different directions. Using Multi-axis DOAS instrument on a stable or movable ground<br />

based platform can also be used to validate DOAS measurements done by satellite instruments.<br />

Figure 2.5: Latitudinal distribution of Stratospheric NO2 VCDs in comparison with SCIAMACHY<br />

results as an example of satellite data validation using ground based MAX-DOAS. The morning<br />

measurements were taken between 5-7 AM O’clock morning and the afternoon ones are between 5-7<br />

PM O’clock afternoon and SCIAMACHY data were collected at 10 AM local equator time.<br />

Background The measurement of trace gases<br />

(identification and quantification) is important for<br />

the investigation of the chemical and physical processes<br />

in the atmosphere. The development of the<br />

Multi Axis DOAS was an important milestone on<br />

the way of DOAS technique evolution. The ability<br />

to direct telescopes to different elevation angles<br />

(multi-axis) allows to emphasize absorption<br />

paths from lowermost atmospheric layers onto the<br />

stratosphere. Measurements from the ground can<br />

provide information on the vertical profile of the<br />

absorbing trace gases under investigation.<br />

Funding IMPRS fellowship<br />

Methods and results Measurements using<br />

Multi-axis DOAS (Differential Optical Absorption<br />

Spectroscopy) on board of a ship platform<br />

(Polarstern research vessel of Alfred-Wegner <strong>Institut</strong>e<br />

<strong>für</strong> Polar- und Meeresforschung) were carried<br />

out successfully in a latitudinal range between<br />

52 ◦ N and 72 ◦ S every year in the last four years<br />

and gave the possibility to measure several trace<br />

gases like NO2, O3 and BrO in the stratosphere<br />

and/or in the marine boundary layer (MBL). The<br />

measurements showed elevated tropospheric NO2<br />

values in the English channel area and the existence<br />

of the tropospheric BrO in the MBL westerly<br />

from Africa in the latitudinal range between<br />

10 ◦ N and 30 ◦ N, which cannot be seen by satellite<br />

instruments because of their higher detection<br />

limit in mid-latitudes. Also a latitudinal cross sectional<br />

distribution of the stratospheric NO2, O3<br />

and BrO were compared to those obtained from<br />

satellite measurements from GOME and SCIA-<br />

MACHY (see figure 2.5). Ground based measurements<br />

from a stable platform in Cabauw in Holland<br />

were performed to retrieve information about<br />

the tropospheric values of trace gases like NO2<br />

and compare them to those obtained from satellite<br />

OMI. Arranging the viewing geometry using<br />

three different telescopes in three viewing planes<br />

can provide some data on the variation of the NO2<br />

concentrations within an OMI pixel. For information<br />

about the satellites see satellite group report.<br />

Outlook/Future work More investigation of<br />

trace gas concentrations in the troposphere and<br />

stratosphere using ground based measurements<br />

from different platforms comparing with results<br />

from satellite measurements for validation of especially<br />

the newer generations SCIAMACHY and<br />

OMI is going to be performed in the near future.<br />

The Multi-axis DOAS will be used on a moving<br />

platform (car) in urban areas to make estimation<br />

of the in and out flux of trace gases from cities besides<br />

measurements for single plumes from powerplants<br />

or industrial activities. This is a promising<br />

application which has already started.


24 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

2.1.6 Imaging DOAS. Imaging of two-dimensional trace gas distributions<br />

Participating scientists Ilia Louban, Nicole Bobrowski<br />

Abstract The two-dimensional trace gas distributions in volcanic plumes was quantitatively determinated.<br />

The measurements at Mt. Etna volcano (spring 2005) and on the island Vulcano (autumn<br />

2004) were carried out with an instrument, based on the principle of Differential Optical Absorption<br />

Spectroscopy combined with an imaging spectrograph (I-DOAS).<br />

Figure 2.6: Two dimensional distribution of sulphur dioxide (SO2) in volcanic plume of Mt. Etna,<br />

measured on May 9. 2005 at 13:30 local time. The image represents a scanned solid angle of (v×h)<br />

13.1 ◦ × 36.4 ◦ of a emission source 10 km away. The Values are slant column densities.<br />

Background Spatial resolved data of trace gas<br />

distributions have a wide spectrum of applications.<br />

In many cases it is essential to be able to<br />

determinate the location of the sources and the<br />

strength of their emissions. Also the dynamical<br />

development and behavior of trace gas concentrations<br />

(trace gas clouds) are very interesting and<br />

important for environmental sciences. The advantage<br />

of the DOAS technique to measure several<br />

trace gases simultaneously can be used to investigate<br />

the chemical balances and processes within<br />

the emissions and high spatial resolution of the<br />

instrument allows to estimate those fluxes.<br />

Funding The developments and investigations<br />

took place within the Project for Development of<br />

Optical Remote Sensing for Volcanic Applications<br />

(DORSIVA), supported by the European Union.<br />

Methods and results Imaging of an object<br />

means to produce a two-dimensional dataset of<br />

spatial information, i.e. each picture element<br />

(pixel) of an image is assigned to a defined solid<br />

angle of the space. In case of imaging spectroscopy<br />

third dimension of data accrued, the spectral information<br />

of each pixel. An imaging spectrograph<br />

allows simultaneous imaging and dispersion of the<br />

light, therefore a two dimensional detector, like<br />

CCD detector is needed.<br />

The instrument optics focus the light from a<br />

defined solid angle (here a column) of space on<br />

the vertical entrance slit of the spectrograph. The<br />

grating inside the spectrograph images spatial and<br />

spectral resolved light on the CCD matrix assigning<br />

the vertical dimension of the detector to the<br />

spatial information and horizontal dimension of<br />

the detector to the spectral information. After the<br />

readout of the CCD, the data of one space column<br />

(”column-shot”) is acquired. Using the horizontal<br />

scanning system a viewing angle up to 70 ◦ can<br />

be scanned. The number of horizontally resolved<br />

pixels is given by the number of acquired ”columnshots”.<br />

The width of those depends on displacement<br />

of the scanning mirror between the ”columnshots”.<br />

The number of vertically resolved pixels<br />

is limited by the number of detector-pixel rows of<br />

the CCD matrix and can be scaled down by averaging<br />

over several detector-pixels rows. After the<br />

acquisition spectral information of each pixel has<br />

to be evaluated with the DOAS method and the<br />

colour coded slant column densities (SCD) can be<br />

assembled into an image (Fig. 2.6).<br />

During the campaigns at Mt. Etna and on<br />

the island Vulcano two-dimensional distributions<br />

of sulphur dioxide (SO2) were measured and the<br />

SO2 flux of several fumaroles were estimated.<br />

Also highly resolved SO2 time series to study the<br />

plume dynamics were performed. Additionally,<br />

two dimensional distributions of bromine monoxide<br />

(BrO) were successfully retrieved. SCD up<br />

to 2.8 · 10 14 Molecules/cm 2 were detected in the<br />

plume of Mt. Etna volcano. By two-dimensional<br />

distributions of SO2 and BrO, depression of the<br />

[SO2]/[BrO] ratio from the center to the age of<br />

the plume was identified. This allows conclusions<br />

about possible ozone involved oxidation processes<br />

of BrO production.<br />

Main publication [Louban, 2005]


2.1. TROPOSPHERIC RESEARCH GROUP 25<br />

2.1.7 Multi Axis Differential Optical Absorption Spectroscopy (MAX-DOAS)<br />

of Trace Gas and Aerosol Distributions<br />

Participating scientist Roman Sinreich<br />

Abstract The combination of MAX-DOAS measurements, i.e. DOAS measurements at different<br />

elevation angles from the ground, and radiative transfer modelling is a suitable method to derive<br />

distributions of trace gases and aerosols.<br />

Figure 2.7: Comparison of MAX-DOAS and in-situ measurements of HCHO in Pinnacle State Park<br />

(USA) at August 3, 2004.<br />

Background For three decades DOAS has been<br />

applied and can be used to measure trace gases<br />

like e.g. NO2, SO2 or HCHO by means of sunlight<br />

[Platt, 1994]. Sunlight passing through the atmosphere<br />

is scattered and absorbed by gas molecules<br />

in the air whereby the absorption occurs at wavelengths<br />

which are characteristic for each trace gas.<br />

The resulting sunlight spectrum contains an absorption<br />

pattern which is suitable to detect and<br />

quantify the according trace gases.<br />

In this study, ground-based DOAS measurements<br />

were performed and their spectra analysed.<br />

One focus was to derive trace gas and aerosol<br />

distributions, by using the measured results and<br />

modelled data.<br />

Methods and results The retrieval of trace<br />

gases by means of DOAS yield Slant Column Densities<br />

(SCDs) which depend upon the concentration<br />

of the according trace gas and the light path.<br />

Since scattered sunlight is measured, the light<br />

path is not readily defined and has to be calculated<br />

by atmospheric radiation transport models.<br />

Furthermore, different elevation angles from the<br />

ground have to be performed in order to get information<br />

on the vertical profile. This method<br />

is called Multi-Axis-DOAS (MAX-DOAS) and allows<br />

to derive gas and aerosol distributions near<br />

the surface.<br />

Aerosol properties can be gained indirectly by<br />

measurements of gas species whose 3-dimensional<br />

distribution is already known and relatively constant.<br />

E.g. O4, whose concentration is proportional<br />

to the square concentration of O2, provides<br />

these qualities. So variations in measured<br />

SCDs are dominated by the aerosol distribution,<br />

which causes different light paths in the atmosphere<br />

[Wagner et al. , 2004].<br />

In summer 2004, a MAX-DOAS network measurement<br />

of 7 sites was performed in New England<br />

(USA) in the framework of ICARTT (International<br />

Consortium for Atmospheric Research on<br />

Transport and Transformation). Thereby, SCDs<br />

of NO2, HCHO, O4 and SO2 could be retrieved<br />

and are in agreement in the main lines with in-situ<br />

measurements at these sites (e.g. see figure 2.7).<br />

Furthermore, an ozone depletion event could be<br />

observed and Glyoxal (C2H2O2) which is a good<br />

tracer for Volatile Organic Compounds could be<br />

detected for the first time by a straylight DOAS<br />

device. Radiative transfer calculations allowed an<br />

estimation of the mixing ratio of about 100 ppt<br />

for Glyoxal at a specific day.<br />

Outlook/Future work Continuation of comparisons<br />

with in-situ measurements, improvement<br />

of the technique of deriving the gas and aerosol<br />

distributions and a MAX-DOAS measurement<br />

campaign in March 2006 in Mexico City.<br />

Main publication [Sinreich et al. , 2005]


26 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

2.1.8 The flying laboratory: DOAS on board the CARIBIC aircraft project<br />

Participating scientists Barbara Dix, Udo Frieß, Thomas Wagner, Ulrich Platt<br />

Abstract CARIBIC is an innovative scientific project to study atmospheric processes on board a<br />

passenger aircraft during long-distance flights. Besides in-situ measurements of various atmospheric<br />

compounds, it also features a Multi-Axis DOAS instrument to detect specific trace gases.<br />

Figure 2.8: The inlet system. Three small black holes in the upper half indicate the position of the<br />

DOAS telescope entrance holes.<br />

Background Halogen compounds and nitrogen<br />

oxides have a significant impact on the global<br />

ozone budget, e.g. reactive bromine and chlorine<br />

compounds cause stratospheric ozone depletion.<br />

Since anthropogenic sources of bromine<br />

compounds are increasing, bromine compounds<br />

are expected to have a growing impact on the<br />

chemical balance of the lower stratosphere in the<br />

future. Halogen species also play an important<br />

role in the troposphere. A possible background<br />

of reactive bromine compounds in the free troposphere<br />

could influence the ozone budget as well<br />

and thus global climate.<br />

Within the frame of CARIBIC (Civil Aircraft<br />

for the Regular Investigation of the atmosphere<br />

Based on an Instrument Container), a new DOAS<br />

(Differential Optical Absorption Spectroscopy) instrument<br />

was built. Besides BrO, it is also able to<br />

detect HCHO, OClO, O3, NO2, water vapor and<br />

O4.<br />

Methods and results The new DOAS instrument<br />

is the only remote sensing instrument within<br />

the CARIBIC project, which comprises 21 instruments<br />

of 11 European institutions in an cargo container,<br />

that has been successfully put into operation<br />

on a new long-range Airbus (A340-600) of<br />

Deutsche Lufthansa in December 2004. Since May<br />

2005 regular flights with fully automated measurements<br />

are performed once a month. A miniaturized<br />

telescope system, which was especially designed<br />

to fit into the inlet system (see Figure<br />

2.8), collects uv-visible scattered sun light from<br />

three different viewing directions (nadir, 10 degrees<br />

above and below the horizon). With this<br />

Multi-Axis technique the separation of boundary<br />

layer, free tropospheric and stratospheric columns<br />

is possible. Trace gases are then detected in<br />

recorded spectra by means of their individual absorption<br />

structures<br />

First results show that the new instrument<br />

performs well. Stratospheric columns of BrO,<br />

NO2 and O3 could be detected as well as tropospheric<br />

water vapor in the tropics. Enhanced levels<br />

of tropospheric NO2 and HCHO during landing<br />

and take-off in big cities such as Buenos Aires,<br />

Guanghzou (China) or Manila were seen due to<br />

anthropogenic pollution. Slant columns of the<br />

oxygen dimer O4 could be derived, which yield<br />

information on the radiative transport. So far no<br />

indications of enhanced BrO levels in the free troposphere<br />

could be found, yielding perhaps to an<br />

evenly distributed BrO background, but these results<br />

are not yet of statistical significance and future<br />

flights have to be awaited.<br />

Outlook/Future work The future work will<br />

consist of exploring the full scientific potential of<br />

this unique DOAS data set, being the first DOAS<br />

measurements on a long-distance aircraft and taking<br />

into account the synergy of other CARIBIC<br />

measurements, e.g. of aerosol, water vapor, ozone<br />

or halocarbons.


2.1. TROPOSPHERIC RESEARCH GROUP 27<br />

2.1.9 Heidelberg ground-based network<br />

Participating scientists Barbara Dix, Udo Frieß, Thomas Wagner, Karin Kreher(1), Ulrich Platt;<br />

(1): National <strong>Institut</strong>e of Water and Atmosphere, Lauder, New Zealand<br />

Abstract The Heidelberg ground-based network consists of four instruments (see Figure 2.9) which<br />

are set up for long-term monitoring. The instruments provide valuable information on global atmospheric<br />

trends and contribute to scientific questions with respect to their individual location.<br />

Figure 2.9: Water vapor measurements at Paramaribo; location of ground-based instruments.<br />

Background The Heidelberg ground-based<br />

network started with measurements in Kiruna,<br />

Sweden, in 1996 and was soon followed by instruments<br />

in the Antarctic. The polar regions have<br />

always been of great scientific interest, since there<br />

the environment is almost free of anthropogenic<br />

influences. While the Artic has become more<br />

polluted, the Antarctic continent still provides<br />

a very clean troposphere, that enables accurate<br />

studies on stratospheric chemistry and transport.<br />

The polar DOAS (Differential Optical Absorption<br />

Spectroscopy) measurements focus on the influence<br />

of halogen compounds on the ozone budget,<br />

with the Antarctic (stratospheric) ozone hole in<br />

spring being its most prominent example. Yet the<br />

ozone hole phenomenon is not restricted to the<br />

southern hemisphere. Severe ozone destruction is<br />

also observed in the Arctic, but usually of smaller<br />

extent due to rather unstable dynamics. Both<br />

hemispheres show also tropospheric halogen activity:<br />

Autocatalytic processes on sea ice cause so<br />

called bromine explosions, which often lead to the<br />

complete destruction of near surface ozone (polar<br />

tropospheric ozone hole).<br />

In 2002 the DOAS instrument in Paramaribo,<br />

Suriname, was setup within a satellite validation<br />

project (Sciamachy validation). At the time of installation,<br />

this instrument was - to our knowledge<br />

- the first continuously operating DOAS instrument<br />

in the tropics. Measurements in the tropics<br />

allow to study global circulation since this is where<br />

most tropospheric air enters the stratosphere.<br />

Funding Sciamachy validation<br />

Methods and results Both Antarctic instruments<br />

and the one in Paramaribo use the Multi-<br />

Axis (MAX)-DOAS technique, where different<br />

viewing directions between zenith and horizon are<br />

scanned sequentially, thus yielding information in<br />

the vertical distribution of trace gases. With<br />

the MAX-DOAS setup many bromine explosion<br />

events were observed in detail. In contrast to measurements<br />

in the Arctic the data base of Arrival<br />

Heights shows no signs of a possible and suggested<br />

global BrO background.<br />

An example of MAX-DOAS measurements in<br />

Paramaribo show significant amounts of water vapor<br />

in the troposphere with rising columns at<br />

lower elevation angles indicating the presence of<br />

water in lower atmospheric layers (see Figure 2.9).<br />

Water has a major impact on radiative forcing and<br />

climate, therefore monitoring water trends is most<br />

valuable in understanding climate change.<br />

All stations contributed to the validation of<br />

satellite data (O3, NO2, BrO) with the Paramaribo<br />

data set adding one of the first BrO long<br />

term measurements in the tropics. The instrument<br />

at German Antarctic station Neumayer is<br />

also part of the international Network for the Detection<br />

of Stratospheric Change (NDSC).<br />

Outlook/Future work Future work will consist<br />

in continuous measurements, data analysis<br />

and interpretation.


28 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

2.1.10 Applicability of light-emitting diodes as light sources<br />

for active DOAS measurements<br />

Participating scientists Christoph Kern, Sebastian Trick, Ulrich Platt<br />

Abstract Light-emitting diodes (LEDs) were tested in respect to their applicability in long path<br />

DOAS (LP-DOAS) measurements. Measurements of NO2 and NO3 were conducted in Heidelberg<br />

using the novel method. Temperature stabilization of the LEDs was found to be essential.<br />

Figure 2.10: (a) Estimated spectral radiance distribution of the Osram 450 W/2 XBO xenon arc lamp,<br />

a Luxeon LXHL-LR3C high power 3W royal blue LED, and a conventional tungsten halogen lamp<br />

(20W). Note that the halogen lamp spectrum is multiplied by 10 in this figure. (b) Spectral radiance<br />

normalized to the electrical input power of the individual sources.<br />

Background To date, xenon arc lamps have established<br />

themselves as the most common light<br />

sources for active DOAS instruments. However,<br />

these have several disadvantages including poor<br />

power efficiency and low lifetime resulting in high<br />

maintenance costs. Modern LEDs potentially represent<br />

a very advantageous alternative. [Ball et al.<br />

, 2004] have already performed first cavity enhanced<br />

absorption spectroscopy (CEAS) measurements<br />

with LED light sources, and we conducted<br />

the first LP-DOAS measurements here.<br />

Funding Diplomarbeit therefore “not applicable”<br />

Methods and results The radiative properties<br />

of a variety of LEDs were characterized,<br />

and parameters such as spectral shape, spectral<br />

range, spectral stability, and how these could<br />

be influenced by environmental factors were analyzed.<br />

A study on the radiative properties of modern<br />

high-power LEDs revealed that despite their<br />

much lower power consumption, they posses spectral<br />

radiances comparable to those of xenon arc<br />

lamps at their peak wavelengths (see Figure 2.10).<br />

The spectra of several LEDs were found to contain<br />

Fabry-Perot etalon-induced spectral structures<br />

that interfered with the DOAS evaluation,<br />

in particular when a constant temperature was<br />

not maintained. It could be shown that LEDs<br />

can successfully be used as light sources in active<br />

DOAS experiments measuring NO2 and NO3<br />

around 450 and 630 nm, respectively. Average detection<br />

limits of 0.3 ppb and 16 ppt, respectively,<br />

were obtained using a 6 km light path in the open<br />

atmosphere.<br />

Outlook/Future work In future LED-DOAS<br />

experiments, emphasis must be put on achieving<br />

higher temperature stability. Also, LEDs are becoming<br />

brighter and more cost-effective, and there<br />

has been considerable recent interest in the development<br />

of UV-LEDs. Devices with emission wavelengths<br />

as low as 250 nm were already demonstrated<br />

in the laboratory. Soon, these will be<br />

available as DOAS light sources, thus enabling the<br />

measurement of many further trace gases such as<br />

BrO, SO2, HCHO, and aromatic hydrocarbons.<br />

Main publications [Kern, 2004],<br />

[Kern et al. , 2005]


2.1. TROPOSPHERIC RESEARCH GROUP 29<br />

2.1.11 Active DOAS measurements of trace gases in the free troposphere<br />

Participating scientist Katja Seitz<br />

Abstract The aim of this thesis was to establish a remote controlled active long–path Differential<br />

Optical Absorption Spectroscopy (DOAS) system with three spectrographs at the research station<br />

Schneefernerhaus on the Zugspitze to measure atmospheric trace gases.<br />

Figure 2.11: Umweltforschungsstation Schneefernerhaus (Zugspitze)<br />

Background Because of its remote location<br />

in the free troposphere the Environmental Research<br />

Station Schneefernerhaus is of special interest<br />

for the measurement of trace gases such as<br />

formaldehyde and ozone. As the Schneefernerhaus<br />

is hard to reach a remote-controlled longpath-<br />

DOAS-system with three spectrographs was established.<br />

Methods and results In order to make<br />

longterm measurements of trace gases such as<br />

ozone and formaldehyde a remote-contr olled<br />

longpath-DOAS (Differential Optical Absorption<br />

Spectroscopy) instrument was established. The<br />

lightbeam of a high pres sure xenon lamp is send<br />

to a retro reflector at a distance of two kilometers<br />

and then back to the Schneefernerhaus. As each<br />

trace gas has a characteristic absorp tion structure<br />

one can determine the concentration of different<br />

trace gases by comparing the reflected light with<br />

a lamp spectra.<br />

After several developements of the system first<br />

measurements were made. It was possible to detect<br />

o zone and formaldehyde. As two different<br />

types of spectrographs were used, their results<br />

were compared.<br />

Outlook/Future work An optical shortcut<br />

system has to be developed. Moreover light emitting<br />

diodes (LEDs) could be used instead of the<br />

xenon lamp, which would be much cheaper and<br />

less effort as the lifetime of a LED is a lot longer<br />

than that of a xenon lamp.<br />

Main publication [Seitz, 2005]


30 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

2.1.12 Long Term Observations of Urban Atmospheric Radical Chemistry<br />

(TURBAN)<br />

Participating scientists Jutta Zingler, Christoph Kern, Daniel Pedersen, Valeri Matveev, Mordechai<br />

Peleg, Ulrich Platt, Menachem Luria<br />

Abstract Using Long Path DOAS and MiniDOAS, seasonal and spatial patterns in the chemistry<br />

of NO3 in an arid urban location are investigated. Its contribution to the transformation and removal<br />

of atmospheric compounds is evaluated. Long term measurements are validated and complemented<br />

by a short term intensive measurement period.<br />

Figure 2.12: Vertical NO3 profiles: Measurement geometry for the MiniDOAS part of this study.<br />

Background The nitrate radical (NO3) is a<br />

key component of nighttime chemistry in the<br />

troposphere and is responsible for the nonphotochemical<br />

production of peroxy radicals and<br />

the transformation of important species such as<br />

nitrogen oxides, VOCs, and ozone. It can be comparable<br />

to the OH radical as a sink for nitrogen<br />

oxides and VOCs. Up to this project, the only<br />

two studies to provide long term nighttime measurements<br />

of NO3 in the boundary layer were conducted<br />

in Germany at a rural coastal site [Heintz<br />

et al. , 1996] and at a rural suburban site [Geyer<br />

et al. , 2001]. One short-term study reported daytime<br />

measurements of NO3 [Geyer et al. , 2003].<br />

Funding German Israeli Foundation for Scientific<br />

Research and Development (G.I.F.)<br />

Methods and results A long term monitoring<br />

station has been established by the Hebrew<br />

University of Jerusalem in the urban center of<br />

Jerusalem, including a Long Path DOAS system<br />

and several monitors for a variety of atmospheric<br />

trace gases and parameters. During an intensive<br />

one month joint field work campaign, IUP Heidelberg<br />

has set up a high end Long Path DOAS<br />

system aiming for quality control, high time resolution<br />

and enhancement of species investigated.<br />

A red LED as alternative light source and new<br />

technology was applied successfully during some<br />

days.<br />

Vertical profiles of NO3 have been measured<br />

using an advanced MiniDOAS system equipped<br />

with a VIS mini-spectrograph (MiniTURBAN).<br />

Stray light spectra acquired during sunrise give<br />

an idea on the concentration profiles in higher atmospheric<br />

layers.<br />

Information on photolytic rates is retrieved<br />

from solar radiation measurements with a spectral<br />

radiometer.<br />

Our long path measurements yielded positive<br />

results for NO3 during almost every night, with<br />

mixing ratios up to 300 ppt. NO3 was found during<br />

a period of very high humidity. Good agreement<br />

could be found comparing NO2 Long Path<br />

DOAS data with in situ monitor results.<br />

Outlook/Future work Evaluation improvement,<br />

intercomparison/correlation of data, quality<br />

control for long term data, profile modelling,<br />

investigation of photolysis parameters.<br />

Main publication in preparation


2.1. TROPOSPHERIC RESEARCH GROUP 31<br />

References<br />

Ball, S. M., Langridge, J. M., & Jones, R. L. 2004. Broadband cavity enhanced absorptions spectroscopy<br />

using light-emitting diodes. Chem. Phys. Lett., 398, 68–74.<br />

Barrie, L. A., & Platt, U. 1997. Arctic tropospheric chemistry. Overview to Tellus special issue, 49B,<br />

450–454.<br />

Bobrowski, N. 2005. Volcanic Gas Studies by MAX-DOAS. Dissertation, <strong>Universität</strong> Heidelberg.<br />

Bobrowski, N., & Filsinger, F. 2005. Mini-MAX-DOAS Manual. <strong>Universität</strong> Heidelberg.<br />

Bobrowski, N., Hönninger, G., Lohberger, F., & Platt, U. 2005. IDOAS: A new monitoring technique<br />

to study the 2D distribution of volcanic gas emissions. J. Volcanol. Geotherm. Res., Accepted for<br />

publishing.<br />

Burkholder, J. B., Curtius, J., Ravishankara, A. R., & Lovejoy, E. R. 2004. Laboratory studies of the<br />

homogeneous nucleation of iodine oxides. Atmos. Chem. Phys., 4, 19–34.<br />

Cauer, H. 2004. Schwankungen der Jodmenge der Luft in Mitteleuropa, deren Ursachen und deren<br />

Bedeutung <strong>für</strong> den Jodgehalt unserer Nahrung (Auszug). Angewandte Chemie 52, 11, 625–628.<br />

Cox, R. A., Bloss, W. J., Jones, R. L., & Rowley, D. M. 1999. OIO and the Atmospheric Cycle of<br />

Iodine. Geophys. Res. Lett., 26 (13), 1857–1860.<br />

Geyer, A., Ackermann, R., Dubois, R., Lohrmann, B., Müller, T., & Platt, U. 2001. Long-term<br />

observation of nitrate radicals in the continental boundary layer near Berlin. Atmos. Env., 35,<br />

3619–3631.<br />

Geyer, A., Alicke, B., Ackermann, R., Martinez, M., Harder, H., Brune, W., Carlo, Piero di, Williams,<br />

E., Jobson, T., Hall, S., Shetter, R., & Stutz, J. 2003. Direct observations of daytime NO3:<br />

Implications for urban boundary layer chemistry. J. Geosphys. Res., 108 (D17), 4368.<br />

Hak, C., Pundt, I., Trick, S., Kern, C., Platt, U., Dommen, J., Ordnez, C., Prvt, A. S. H., Junkermann,<br />

W., Astorga-Llorns, C., Larsen, B. R., Mellqvist, J., Strandberg, A., Yu, Y., Galle, B., Kleffmann,<br />

J., Lörzer, J. C., Braathen, G. O., & Volkamer, R. 2005. Intercomparison of four different in-situ<br />

techniques for ambient formaldehyde measurements in urban air. Atmos. Chem. Phys. Discuss., 5,<br />

2897–2945.<br />

Heintz, F., Platt, U., Flentje, H., & Dubois, R. 1996. Long-term observation of nitrate radicals at the<br />

Tor Station, Kap Arkona (Rügen). J. Geophys. Res., 101 (D17), 22891–22910.<br />

Hoffmann, T., O’Dowd, C. D., & Seinfeld, J. H. 2001. IO homogeneous nucleation. An explanation<br />

for coastal new particle formation. Geophys. Res. Lett., 28 (10), 1949–1952.<br />

Kern, C. 2004. Applicability of light-emitting diodes as light sources for long path DOAS measurements:<br />

A feasibility study. Diplomarbeit, <strong>Universität</strong> Heidelberg.<br />

Kern, C., Trick, S., Rippel, B., & Platt, U. 2005. Applicability of light-emitting diodes as light sources<br />

for active DOAS measurements. Appl. Opt., Accepted for publishing.<br />

Leck, C., & Bigg, E. K. 1999. Aerosol production over remote marine areas - A new route. Geophys.<br />

Res. Lett., 26, 3577–3580.<br />

Lee, J. S., Kim, Y. J., Kuk, B., Geyer, A., & Platt, U. 2005. Simultaneous Measurements of Atmospheric<br />

Pollutants and Visibility with a Long-Path DOAS System in Urban Areas. Environ. Monit.<br />

Assess., 104, 281–293.<br />

Lindberg, S., Brooks, S., Lin, C. J., Scott, K. J., Landis, M. S., Stevens, R. K., Goodsite, M., &<br />

Richter, A. 2002. Dynamic Oxidation of Gaseous Mercury in the Arctic Troposphere at Polar<br />

Sunrise. Environ. Sci. Technol., 36, 1245–1256.<br />

Louban, I. 2005. Zweidimensionale Aufnahmen von Spurenstoff-Verteilungen. Diplomarbeit, <strong>Universität</strong><br />

Heidelberg.<br />

O’Dowd, C., Jimenez, J. L., Bahreini, R., Flagan, R. C., Seinfeld, J. H., Hämeri, K., Pirjola, L., ans<br />

S. G. Jennings, M. Kulmala, & Hoffmann, T. 2002. Marine aerosol formation from biogenic iodine<br />

emissions. Nature, 417, 632–636.


32 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

Peters, C. 2005. Studies of Reactive Halogen Species (RHS) in the Marine and mid-Latitudinal Boundary<br />

Layer by Active Longpath Differential Optical Absorption Spectroscopy. Dissertation, <strong>Universität</strong><br />

Heidelberg.<br />

Peters, C., Pechtl, S., Stutz, J., Hebestreit, K., Hönninger, G., Heumann, K. G., Schwarz, A., J.,<br />

Winterlik, & Platt, U. 2005. Reactive and organic halogen species in three different European<br />

coastal environments. Atm. Chem. and Phys. Disc., 5, 6077–6126.<br />

Platt, U. 1994. Differential optical absorption spectroscopy (DOAS). In: Sigrist, M. W. (ed), Air<br />

Monitoring by Spectroscopic Techniques. New York: John Wiley.<br />

Platt, U., & Hönninger, G. 2003. The Role of Halogen Species in the Troposphere. Chemosphere 52,<br />

2, 325–338.<br />

Platt, U., & Janssen, C. 1996. Observation and role of the free radicals NO3, ClO, BrO and IO in the<br />

Troposphere. Faraday Discuss., 100, 175–198.<br />

Platt, U., Allan, W., & Lowe, D. 2004. Hemispheric Average Cl Atom Concentration from 13 C/ 12 C<br />

Ratios in Atmospheric Methane. Atmos. Chem. Phys., 4, 2393–2399.<br />

Platt, U., Pfeilsticker, K., & Vollmer, M. 2005. Chapter 24: Atmospheric Optics. In: Träger, F. (ed),<br />

Springer Handbook of Lasers and Optics. Heidelberg: Springer.<br />

Pundt, I., Mettendorf, K. U., Laepple, T., Knab, V., Xie, P., Lösch, J., von Friedeburg, C., Platt,<br />

U., & Wagner, T. 2005. Measurements of trace gas distributions by Long-Path DOAS-Tomography<br />

during the motorway campaign BAB II: experimental setup and results for NO2 (BAB II special<br />

issue). Atmos. Environ., 39(5), 967–975.<br />

Roscoe, H.K., Kreher, K., & Friess, U. 2001. Ozone loss episodes in the free Antarctic troposphere,<br />

suggesting a possible climate feedback. Geophys. Res. Lett., 28, 2911–2914.<br />

Seitz, K. 2005. Spektroskopische Langzeitmessungen von Spurengasen in der freien Troposphäre.<br />

Diplomarbeit, <strong>Universität</strong> Heidelberg.<br />

Sinreich, R., Frieß, U., Wagner, T., & Platt, U. 2005. Multi Axis Differential Optical Absorption<br />

Spectroscopy (MAX-DOAS) of Gas and Aerosol Distributions. Farady Discuss., 153 – 164.<br />

Stutz, J., Hebestreit, K., Alicke, B., & Platt, U. 1999. Chemistry of halogen oxides in the troposphere:<br />

comparison of model calculations with recent field data. J. Atmos. Chem., 34, 65–85.<br />

Tas, E., Peleg, M., Matveev, V., Zingler, J., & Luria, M. 2005. Frequency and extent of bromine oxide<br />

formation over the Dead Sea, Israel. J. Geosphys. Res., 110, D11304.<br />

Volkamer, R., Barnes, I., Platt, U., Molina, L. T., & Molina, M. J. 2004. Remote Sensing of Glyoxal<br />

by Differential Optical Absorption Spectrosocopy (DOAS): Advancements in Simulation Chamber<br />

and Field Experiments. In: Rudzinski, K., & Barnes, I. (eds), NATO Advanced Research Workshop<br />

of Environmental Simulation Chambers - Application to Atmospheric Chemical Processes, vol.<br />

NATO Sciences Series, IV. Earth and Environmental Sciences. Zakopane, Poland: Kluwer Academic<br />

Publishers.<br />

Volkamer, R., Spietz, P., Burrows, J. P., & Platt, U. 2005. High-resolution absorption cross-section of<br />

Glyoxal in the UV/vis and IR spectral ranges. J. Photoch. Photobio. A: Chemistry, 172, 35 – 46.<br />

von Friedeburg, C., Pundt, I., Mettendorf, K. U., Wagner, T., & Platt, U. 2005. Multi-AXis-(MAX)<br />

DOAS Measurements of NO2 during the BAB II Motorway Emission Campaign, (BAB II special<br />

issue). Atmos. Environ., 39(5), 977–985.<br />

von Glasow, R., & Crutzen, P.J. 2004. Model study of multiphase DMS oxidation with a focus on<br />

halogens. Atmos. Chem. Phys., 4, 589–608.<br />

von Glasow, R., von Kuhlmann, R., Lawrence, M. G., Platt, U., & Crutzen, P.J. 2004. Impact of<br />

reactive bromine chemistry in the troposphere. Atmos. Chem. Phys., 4, 2481 – 2497.<br />

Wagner, T., Dix, B., v. Friedeburg, C., Frieß, U., Sanghavi, S., Sinreich, R., & Platt, U. 2004.<br />

MAX-DOAS O4 measurements: A new technique to derive information on atmospheric aerosols -<br />

Principles and information content. J. Geophys. Res., 109, D22205.


2.1. TROPOSPHERIC RESEARCH GROUP 33<br />

Wenig, M., Jähne, B., & Platt, U. 2005. Operator Representation as a new differential optical absorption<br />

spectroscopy formalism. Appl. Opt., 44(16), 3246–3253.<br />

Wennberg, P.O., Hanisco, T. F., Jaegle, L., Jacob, D. J., Hintsa, E. J., Lanzendorf, E. J., Anderson,<br />

J.G., Gao, R. S., Keim, E. R., Donnelly, S. G., Negro, L. A. Del, Fahey, D. W., McKeen, S. A.,<br />

Salawitch, R. J., Webster, C. R., May, R. D., Herman, R. L., Proffitt, M. H., Margitan, J. J., Atlas,<br />

E. L., Schauffler, S. M., Flocke, F., McElroy, C. T., & Bui, T. P. 1998. Hydrogen radicals, nitrogen<br />

radicals, and the production of O3 in the upper troposphere. Science, 279, 49–53.<br />

Zingler, J., & Platt, U. 2005. Iodine Oxide in the Dead Sea Valley: Evidence for inorganic sources of<br />

boundary layer IO. J. Geosphys. Res., 110, D07307.


2.2. STRATOSPHERIC OZONE 35<br />

2.2 Stratospheric Ozone<br />

Participating scientists Pfeilsticker, K., A. Butz, M. Dorf, K. Grunow (*), L. Kritten, A. Lindner,<br />

U. Reichl, J. Schwärzle, B. Simmes, and F. Weidner, (*) also with FU-Berlin<br />

Abstract Stratospheric research at the IUP concentrates on an improved understanding of the<br />

photochemical processes controlling stratospheric ozone and its link to climate.<br />

Figure 2.13: Recent history of stratospheric organic (Brorg y = CH3Br, various man-made halones,<br />

and shorter lived organo-bromines) and inorganic (Brin y ) bromine. The open square denoted Brin y<br />

inferred from balloon-borne BrO measurements of the LPMA/DOAS balloon payload since 1996. Note<br />

that bromine is responsible for ∼ 35% of the recent stratospheric loss in ozone with an anticipated<br />

increasing fraction of the total in the future (adopted from M. Dorf, PhD thesis 2005).<br />

Scientific objectives of our stratospheric ozone research include investigation on:<br />

• the photochemistry and budget of upper tropospheric and stratospheric bromine (BrO, Bry)<br />

and its relevance to stratospheric ozone (see figures 2.13 and 2.2.1).<br />

• the photochemistry and budget of upper tropospheric and stratospheric iodine (IO, OIO, Iy)(see<br />

2.2.2 and 2.2.4)<br />

• the stratospheric chemistry and budget of odd nitrogen (NO, NO2, HNO3, ClONO2) (see<br />

2.2.2)<br />

• the partitioning and photochemistry of chlorine and bromine in the high latitude stratosphere<br />

and the assessment of the instantaneous in-situ ozone loss rate (see 2.2.2)<br />

• prominent natural and anthropogenic sources to the trace gas composition of the tropical<br />

tropopause and lowermost stratosphere (TTL/LMS) (see 2.2.4 and 2.2.5)<br />

• the temporal and spatial dependence of stratospheric radicals concentrations (e.g., NO2/N2O5,<br />

BrO/OClO, . . . ) (see 2.2.3)<br />

• the validation of remote sensing satellite instruments, such as ILAS/ADEOS, POAM II and<br />

III, SAGE II and III, ODIN/OSIRIS, GOME/ERS-2, and SCIAMACHY/ENVISAT satellite<br />

instruments (see 2.2.1 and 2.2.2)<br />

Methods The research objectives imply to probe the stratosphere by high altitude (∼ 40 km)<br />

balloon soundings. For that purpose the research group is operating (1) a lab-built two channel<br />

UV/vis spectrometer with which direct Sun measurements are made, and (2) a novel LIMB scanning<br />

UV/vis spectrometer. Both spectrometers are deployed on the joint French/German LPMA/DOAS<br />

(Laboratoire de Physique Moléculaire et Applications/Differential Optical Absorption Spectroscopy)<br />

balloon payload. Jointly with our direct Sun measurements, our French partner operates a near-IR<br />

Fourier Transform Spectrometer with which mid-IR absorbing gases are measured. Balloon flights<br />

are regularly performed at high (Kiruna/Sweden), mid (Aire sur l’Adour/France) and low latitudes


36 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

(Teresina/Brazil). Interpretation of the measurements also involves radiative transfer studies and 1-D<br />

photochemical modelling on air mass trajectories provided by our partner Meteorologisches <strong>Institut</strong>,<br />

FU-Berlin, Berlin, Germany. The model’s required initialisation is provided through outputs from a<br />

3-D chemistry model (CTM-SLIMCAT) run by the <strong>Institut</strong>e for Atmospheric Science, School of Earth<br />

and Environment, University of Leeds, Leeds, UK.<br />

Our scientific objectives are primarily achieved through measurements of stratospheric radicals (O3,<br />

NO2, BrO, OClO, IO, OIO, . . . ) and related trace gases (CH4, N2O, HCl, NO, HNO3, ClONO2,<br />

. . . ) and the interpretation of the results with respect to the photochemistry of stratospheric ozone.<br />

Major research objectives involve studies of the processes leading to the formation of the ozone hole<br />

in polar winter, the global decline in stratospheric ozone and since recently the photochemistry and<br />

transport of the tropical tropopause layer (TTL) and lowermost stratosphere (LMS). The research of<br />

the group is largely contributing to various international assessments on stratospheric ozone (WMO<br />

report in 1998, 2002, and 2006), organized by the World Meteorological Organisation (WMO).<br />

Field Campaigns & Studies<br />

1. March 04: a high latitude balloon campaign at Kiruna/Sweden (67.9 o N, 21.2 o W) within the<br />

ENVISAT/SCIAMACHY validation<br />

2. Nov./Dec. 2004: a tropical balloon campaign at Teresina/Brazil (5.1 o S, 42.9 o W) within the<br />

ENVISAT/SCIAMACHY validation<br />

3. June, 2005: a tropical balloon campaign at Teresina/Brazil (5.1 o S, 42.9 o W) within the EN-<br />

VISAT/SCIAMACHY validation<br />

International Cooperation The research group closely cooperates with the following institutions<br />

as e.g., documented in joint peer-reviewed publications.<br />

(1) Forschungszentrum Jülich GmbH, <strong>Institut</strong> <strong>für</strong> Chemie und Dynamik der Geosphare ICG-I: Stratosphäre,<br />

Jülich, Germany (2) Laboratoire de Physique Moléculaire pour l’Atmosphere et l’Astrophysique<br />

(LPMAA), Université Pierre et Marie Curie, Paris, France (3) Harvard-Smithsonian Center for Astrophysics,<br />

Cambridge, USA (4) <strong>Institut</strong>e for Atmospheric Science, School of Earth and Environment,<br />

University of Leeds, Leeds, UK (7) Meteorologisches <strong>Institut</strong>, Freie <strong>Universität</strong> Berlin, Berlin, Germany<br />

(6) Service d’Aeronomie du CNRS, Verrieres le Buisson, France (7) Belgian <strong>Institut</strong>e for Space<br />

Aeronomy (BIRA-IASB), Brussels, Belgium (8) Jet Propulsion Laboratory (JPL), Pasadena, USA<br />

(9) <strong>Institut</strong>e for Atmosphere and Environment, J.W. Goethe University Frankfurt, Frankfurt, Germany<br />

(10) European Space Agency (ESA), Nordwijk, Netherland, (11) <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong> und<br />

Fernerkundung, University of Bremen, Bremen, Germany (12) Chemistry Department, University of<br />

Cambridge, Cambdrige, UK, (13) <strong>Institut</strong> <strong>für</strong> Meterologie und Klima (IMK) Forschungszentrum <strong>Karls</strong>ruhe,<br />

<strong>Karls</strong>ruhe, Germany<br />

Outlook/Future work Future work will concentrate on (1) time resolved measurements of stratospheric<br />

radicals, and (2) to continue our budget and trend studies on stratospheric bromine and iodine.<br />

Future studies will also be devoted to the validation of existing (ENVISAT/SCIAMCHY) and future<br />

satellite instruments (Metop/GOME-2 and IASI).<br />

Funding comes through research contracts with European Community (EU-EVK2-CT-2000-00059,<br />

and 505390-GOCT-CT-2004), the BundesMinisteriumForschungs&Technologie (BMBF) through the<br />

DLR (DLR-50FE0017) and the Deutsche Forschungsgemeinschaft (DFG PF384/3-1).<br />

Publications<br />

Peer reviewed publications:<br />

1. Butz et al. [2005]<br />

2. Canty et al. [2005]<br />

3. Dufour et al. [2005]<br />

4. Hendrick et al. [2004]<br />

5. Vandaele et al. [2005]<br />

6. Weidner et al. [2005]


2.2. STRATOSPHERIC OZONE 37<br />

PhD theses:<br />

1. Dorf [2005]<br />

2. Weidner [2005]<br />

Diploma theses:<br />

1. Reichl [2005]<br />

2. Schwärzle [2005]<br />

Invited Talks<br />

1. Butz [2005]


38 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

2.2.1 Investigation of Inorganic Stratospheric Bromine<br />

Participating scientists Dorf, M., A. Butz, F. Weidner, and K. Pfeilsticker<br />

Abstract Balloon-borne DOAS (Differential Optical Absorption Spectroscopy) bromine monoxide<br />

(BrO) measurements and model simulations are used to investigate the inorganic stratospheric<br />

bromine chemistry and to validate BrO limb profiling from the new SCIAMACHY instrument on the<br />

European Envisat (ENVIronment SATellite) satellite.<br />

Morning Evolution Evening Evolution<br />

Time Time<br />

Figure 2.14: Colour-coded model concentration field of BrO as a function of height and SZA, for<br />

a DOAS balloon flight. Left and right panels show the morning and evening evolution of BrO<br />

respectively. The black lines in the left panel represent the line-of-sight of a SCIAMACHY limb<br />

scan. In the right panel the observation geometry of the DOAS measurements is shown. The thick<br />

black line represents the trajectory of the balloon and the thin black lines indicate the optical path<br />

from the Sun to the balloon instrument for measurements during ascent and solar occultation.<br />

Background Inorganic bromine (BrY) is the<br />

second most important halogen affecting stratospheric<br />

ozone. Although much less abundant than<br />

chlorine, stratospheric bromine currently contributes<br />

about 25 % to global ozone loss. During<br />

daylight the most abundant stratospheric bromine<br />

species is BrO, which accounts for 60 − 70 %<br />

of total BrY and is also the most feasible inorganic<br />

bromine species for detection. Balloonborne<br />

DOAS BrO measurements are used for validation<br />

of the SCIAMACHY satellite instrument.<br />

Funding This work was conducted within ESA<br />

contracts AO 146 and AO 465. Funding came<br />

from the BundesMinisterium <strong>für</strong> Bildung und<br />

Forschung (BMBF), contract DLR-50EE0017.<br />

Methods and results BrO is subject to considerable<br />

diurnal variation. Validation thus requires<br />

either perfect collocation of the validation<br />

observation with the satellite profiling, or other<br />

methods to account properly for temporal or spatial<br />

mismatches between both sets of observations<br />

and for their different viewing geometry (see<br />

figure 2.14). Photochemical modelling along air<br />

mass trajectories, which match the balloon with<br />

SCIAMACHY observations are used to account<br />

for these discrepancies and to generate a BrO<br />

profile validation set. First comparisons of SCIA-<br />

MACHY limb measurements with high precision<br />

DOAS BrO profiles show poor agreement, especially<br />

below 20 km, which is presently the most<br />

interesting region for bromine chemistry.<br />

Outlook/Future work<br />

• Investigation of the upper troposphere /<br />

lower stratosphere bromine budget<br />

• Investigation of the composition of organic<br />

bromine source gases<br />

• Bromine trend in the stratosphere<br />

• Coupling of bromine and chlorine chemistry<br />

Main publication Dorf, M., Investigation of<br />

Inorganic Stratospheric Bromine using Balloon-<br />

Borne DOAS Measurements and Model Simulations,<br />

PhD thesis at the University of Heidelberg,<br />

Heidelberg, Germany, 2005.


2.2. STRATOSPHERIC OZONE 39<br />

2.2.2 Stratospheric photochemistry of ozone, nitrogen and chlorine species<br />

Participating scientists at IUP Heidelberg Butz, A., M. Dorf, F. Weidner, and K. Pfeilsticker<br />

Abstract In the recent past the LPMA/DOAS balloon payload has conducted several stratospheric<br />

balloon flights at various locations and in different seasons. The inferred abundances of stratospheric<br />

ozone (O3) and nitrogen dioxide (NO2) are checked for internal consistency and compared to correlative<br />

data measured by the satellite borne instrument SCIAMACHY.<br />

Figure 2.15: Relative deviations between satellite (retrieved by IUP Bremen) and balloon borne measurements<br />

of O3 (left panel) and NO2 (right panel) vertical profiles. Observation sites and conditions are indicated in the<br />

legend. The mean deviation of all coincident data in the 20 km – 31 km altitude is 4.3% with 10.8% standard<br />

deviation for O3 and 1.8% with 12.4% standard deviation for NO2. The grey lines indicate the mean and the<br />

one and two times standard deviation boundaries with respect to the 20 km – 31 km altitude range. Note the<br />

broken abscissa.<br />

Background Nitrogen oxides dominate the catalytic<br />

destruction of stratospheric O3 between 25<br />

and 40 km altitude. Thus, NO2 and O3 measurements<br />

are of primary importance to study<br />

stratospheric photochemistry. Recent studies indicate<br />

that for selected geophysical conditions the<br />

agreement between measured and modeled O3 and<br />

NO2 is better than 10%. Accordingly, measurements<br />

of high accuracy are required to constrain<br />

or to be compared with photochemical models.<br />

Our study aims at estimating the accuracy of<br />

state-of-the-art remote sensing measurements of<br />

O3 and NO2.<br />

Funding The present work has been supported<br />

by ESA, BMBF, DLR and the European Union.<br />

Methods and results Abundances of stratospheric<br />

O3 and NO2 inferred from traditional<br />

solar occultation measurements of the<br />

LPMA/DOAS balloon payload are checked for internal<br />

consistency and subsequently compared to<br />

collocated observations of the SCanning Imaging<br />

Absorption spectroMeter for Atmospheric CHartographY<br />

(SCIAMACHY) onboard the European<br />

Envisat satellite. Our comparison scheme accounts<br />

for the temporal and spatial mismatch (airmass<br />

trajectory modell) as well as for the differing<br />

photochemical conditions (1D chemistry modell)<br />

between the balloon and the satellite borne observations.<br />

The internal agreement of the balloon borne<br />

measurements is 10% and 20% for O3 and NO2,<br />

respectively. Typical deviations between SCIA-<br />

MACHY and the balloon borne data amount to<br />

20% for both gases in the 20 to 30 km altitude<br />

range, see figure (2.15). Below 20 km the agreement<br />

worsens mainly due to lower sensitivity of<br />

the satellite retrieval.<br />

Outlook/Future work<br />

• Extension of the O3 and NO2 validation<br />

study to tropical latitudes<br />

• Case studies of the stratospheric nitrogen<br />

and chlorine budget/partitioning and implications<br />

for ozone loss<br />

• Abundance of iodine radicals in the tropical<br />

upper troposphere and stratosphere<br />

Main publication Butz, A. et al., Intercomparison<br />

of Stratospheric O3 and NO2 abundances<br />

retrieved from balloon borne direct sun observations<br />

and Envisat/SCIAMACHY limb measurements,<br />

Atmos. Chem. Phys. Disc. 5, 10747–<br />

10797, 2005.


40 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

2.2.3 Photolytic lifetime of stratospheric N2O5<br />

Participating scientists Kritten, L., F. Weidner, A. Butz, B. Simmes, M. Dorf, U. Reichl, and K.<br />

Pfeilsticker<br />

Abstract During one of the first international measurement campaigns in the tropics (Teresina,<br />

Brazil), balloon borne measurements of upper tropospheric and stratospheric trace gases were made<br />

using a recently developed UV/visible spectrometer which operates in limb viewing geometry and<br />

allows to infer time resolved (Weidner et al., 2005) vertical profiles.<br />

Background The amount and partitioning of<br />

stratospheric NOx (NO, NO2 and NO3) and<br />

NOy (NOx, N2O5, HNO3, ClONO2, HO2NO2<br />

and BrONO2) largely govern ozone (O3) photochemistry<br />

in the mid-stratosphere (25-40km).<br />

During daytime, NOx is supplied by the photochemical<br />

decay of the reservoir molecule N2O5.<br />

Monitoring the relative diurnal increase of NO2<br />

thus provides information on the photolytic lifetime<br />

of N2O5.<br />

Funding comes through ESA, BMBF, DLR,<br />

and the European Union.<br />

Methods and results In the framework of international<br />

measurement campaign dedicated to<br />

ENVISAT/SCIAMACHY validation three stratospheric<br />

balloon flights have been performed in<br />

tropical latitudes near Teresina, Northern Brazil,<br />

onboard the MIPAS, LPMA/DOAS and IASI balloon<br />

payloads. Our UV/vis spectrometer took<br />

spectra with scanning elevation angle (0 – -6 o )<br />

during balloon float. Slant column densities<br />

(SCDs) of O3 and NO2 were inferred from measurements<br />

conducted during IASI balloon flight.<br />

Using a Radiative Transport model (Tracy, developed<br />

at IUP Heidelberg) SCDs can be simulated<br />

according to our viewing geometry with an appro-<br />

priate trace gas profile as input.<br />

Figure 2.16 shows the inferred temporal<br />

change in measured stratospheric O3 and NO2 for<br />

the LPMA-IASI flight at Timon/Brazil on June<br />

30, 2005. As expected for the tropical stratosphere,<br />

while the inferred stratospheric ozone does<br />

not change much (< 10% ), NO2 largely increases<br />

(a factor of 2) over the course of the day, primarily<br />

due to the photolysis of the nighttime reservior<br />

species N2O5 into NO2 and NO3. The observed<br />

increase in NO2 can be used to test calculated<br />

N2O5 photolysis frequencies as a function of the<br />

actinic flux and the still uncertain temperature<br />

depndence of the N2O5 absorption cross section.<br />

Outlook/Future work<br />

• Analysis of all three balloon flights at<br />

Teresina for UV/vis absorbing gases such<br />

as O3, NO2, BrO, OClO, IO, OIO, and<br />

CH2O.<br />

• Preparation of and participation in future<br />

measurement campaigns (Kiruna, January<br />

2006)<br />

Main publication Kritten, L., et al., The photolytic<br />

lifetime of stratospheric N2O5, GRL, (in<br />

preparation), 2005.<br />

Figure 2.16: Inferred temporal change stratospheric O3 and NO2 concentrations as a function of<br />

time, solar zenith angle and height for the LPMA-IASI flight at Timon/Brazil on June 30, 2005.<br />

Note while the ozone field is almost constant with time and space, the NO2 concentrations increase<br />

at all altitudes with the largest increase seen in the 30 - 35 km range. Also shown are 2 collocated<br />

SCIAMCHY/ENVISAT observations on June 29, UT 12:16 (# orbit 17412) and on July 1, UT 12:53<br />

(# orbit 17441) which can be validated with the mini-DOAS observations.


2.2. STRATOSPHERIC OZONE 41<br />

2.2.4 Spectroscopic measurements of halogen oxides in the marine boundary<br />

layer in Alcântara/Brazil<br />

Participating scientists Schwärzle, J., A. Lotter, and K. Pfeilsticker<br />

Abstract Since the discovery of stratospheric ozone loss due to these species, the atmospheric<br />

photochemistry of reactive halogen species has become of particular concern. Their fate and behavior<br />

in the atmosphere is still uncertain. During a campaign carried out in Northeastern Brazil, IO was<br />

detected for the first time in a tropical coastal region.<br />

Figure 2.17: Mixing ratio of IO, measured at Alcântara/Brazil. Night time is indicated by grey<br />

background, tidal height is shown in blue in order to point out a possible correlation between tidal<br />

height, daylight and mixing ratios of IO<br />

Background Since reactive halogens have been<br />

detected at different sites all over the world (arctic,<br />

mid-latitudes), the global impact of halogen<br />

oxides on the chemistry of tropospheric ozone is<br />

an arising question. It is of special importance in<br />

the tropics as there is fast vertical convection of<br />

air from the boundary layer into the lower stratosphere.<br />

Funding came through Deutsche Forschungsgemeinschaft<br />

(DFG-PF 384/1-2 and 2-3).<br />

Methods and results The measurements were<br />

conducted by active long-path Differential Optical<br />

Absorption Spectroscopy (DOAS) near the<br />

ocean-surface during a field campaign held in<br />

Alcântara/Northeastern Brazil from December<br />

2004 until January 2005.<br />

Mixing ratios of up to 0.82 ppt of IO were determined<br />

within the IO-absorption-bands in the<br />

spectral range of 418–438 nm. Possible sources of<br />

the inorganic iodine in the marine boundary layer<br />

are the photochemical decay of short-lived organic<br />

iodine emitted from the biologically active oceanic<br />

shelf region (e.g. mangroves), or at lower concentrations<br />

by long-range transport of these species<br />

from the open ocean.<br />

Absorption structures in the range of 320–<br />

350 nm were analyzed for the absorption of<br />

bromine oxide, which could not be detected.<br />

Outlook/Future work<br />

• Identification of iodine source gases<br />

• Abundances of IO in the coastal and continental<br />

tropics<br />

• Determining possible impact of IO on tropospheric/stratospheric<br />

ozone<br />

Main publication Schwärzle, J., Spektroskopische<br />

Messung von Halogenoxiden in<br />

der marinen atmosphrischen Grenzschicht in<br />

Alcântara/Brasilien, Staatsexamensarbeit, University<br />

of Heidelberg, Heidelberg, Germany, 2005.


42 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

2.2.5 Ground-based direct Sun UV/vis spectroscopy in Timon/Northeastern<br />

Brazil: Comparison of tropospheric air mass pollution in the dry and<br />

wet season<br />

Participating scientists Reichl U., A. Butz, M. Dorf, L. Kritten, A. Lindner, B. Simmes, F.<br />

Weidner, and K. Pfeilsticker,<br />

Abstract: The impact of biomass burning on the concentration of tropospheric pollutants is investigated<br />

by comparisons of direct Sun UV/Vis DOAS measurements (Differential Optical Absorption<br />

Spectroscopy) at TIMON/North Eastern Brazil (5.1 o S, 42.9 o W) at the end of dry season in Nov<br />

2004 and after the rainy season in June 2005. Natural and anthropogenic contributions to pollutants<br />

(e.g. CH2O and NO2) to the tropical continental troposphere are assessed and corresponding species<br />

remotely sensed by the ENVISAT/SCIAMACHY instrument are validated. Biomass emission ratios<br />

for NO2 and CH2O are also inferred.<br />

Figure 2.18: Tropospheric vertical amount (VCD) of<br />

NO2 (upper two panels) and CH2O (lower two panels)<br />

during the dry season sunset (left panels) and end of<br />

the wet season (right panels) at TIMON/North Eastern<br />

Brazil (5.1 o S, 42.9 o W). The vertical lines marked<br />

by are (1) the average NO2 at the end-of wet season,<br />

(2) the average NO2 at the end-of dry season, (3) the<br />

average CH2O at the end-of wet season, and (4) the<br />

average CH2O at the end-of dry season. Considering<br />

the most likely emission scenario for TIMON, the<br />

difference of (2) - (1), and (4) - (3) can be ascribed<br />

to end-of the dry season biomass burning emissions.<br />

Accordingly, the baselines in the left panels are being<br />

due to either CH2O formed during hydrogen carbon<br />

related oxidation, or NOx related emission by anthropogenic<br />

emissions.<br />

Background In the tropics biomass burning is<br />

a prominent source of atmospheric pollutants. For<br />

further assessments on the potential impact of<br />

biomass burning on tropospheric ozone and air<br />

quality estimates of emission factors of certain<br />

pollutants, i.e. emitted pollutant mass per mass<br />

biomass burned, is of primary interest [Andreae<br />

& Merlet, 2001].<br />

Methods and results Ground-based direct<br />

sun spectroscopy of NO2 and CH2O<br />

were performed within the balloon-borne EN-<br />

VISAT/SCIAMACHY validation activities in<br />

Northeastern Brazil during the end of the dry season<br />

(Nov. 2004) and wet season (June 2005). The<br />

spectroscopic measurements indicate distinct features<br />

of biomass burning on the tropospheric composition<br />

(compare e.g. the left and right panels<br />

in Figure 2.18) in agreement with recent observations<br />

of ENVISAT/SCIAMACHY instrument (see<br />

section 2.5.12). Our observations indicate typical<br />

increases (∆) in the vertical column amounts<br />

of ∆NO2 = 4.8 · 10 15 /cm 2 and ∆CH2O =<br />

9.0 · 10 15 /cm 2 , respectively for the dry versus<br />

wet season tropical boundary layer. These imply<br />

emission ratios E(∆NOx/∆CH2O) = 1.6 ± 1,<br />

a result being in good agreement with recent<br />

estimates (0.64 to 1.64) for tropical forest fires<br />

(Andreae & Merlet [2001]). The elevated baseline<br />

concentrations (right panels in 2.18) for CH2O<br />

indicate the important role oxidation of naturally<br />

emitted hydrogen carbons plays and for NO2<br />

the influence of anthropogenic activity (traffic related<br />

fossil fuel consumption) related emissions<br />

on the photochemistry of tropospheric ozone and<br />

air quality.<br />

Funding came through research contracts with<br />

the BundesMinisteriumForschungs&Technologie<br />

(BMBF) through the DLR (DLR-50FE0017).<br />

Outlook/Future work will concentrate on a<br />

more thorough characterization of biomass and<br />

fossil fuel related emissions on the photochemistry<br />

of tropospheric ozone and air quality in the tropics.<br />

Validation of remotely sensed tropospheric<br />

pollution will also be conducted.<br />

Main publication Reichl, U., Groundbased<br />

direct Sun UV/vis spectroscopy in Timon/Northeastern<br />

Brazil: Comparison of tropospheric<br />

air mass pollution in the dry and wet<br />

season, Diploma thesis at the University of Heidelberg,<br />

Heidelberg, Germany, 2005.


2.2. STRATOSPHERIC OZONE 43<br />

References<br />

Andreae, M.O., & Merlet, P. 2001. Emission of trace gases and aerosols from biomass burning. Global<br />

Biochem. Cycles, 15, 4, 955 – 966.<br />

Butz, A. 2005. LPMA/DOAS: Balloon based SCIAMACHY validation example: O3 and NO2 vertical<br />

profiles. SCIAMACHY Science Advisory Group 32, Delft, Netherlands.<br />

Butz, A., Bösch, H., Camy-Peyret, C., Chipperfield, M., Dorf, M., Dufour, G., Grunow, K., Jeseck,<br />

P., Kühl, S., Payan, S., Pepin, I., Pukite, J., Rozanov, A., von Savigny, C., Sioris, C., Wagner, T.,<br />

Weidner, F., & Pfeilsticker, K. 2005. Inter-comparison of Stratospheric O3 and NO2 abundances retrieved<br />

from balloon borne direct sun observations and Envisat/SCIAMACHY limb measurements.<br />

Atmos. Chem. Phys. Disc., 5, 10747 – 10797.<br />

Canty, T., Salawitch, R.S., Renard, J.B., Reviere, E.D., Pfeilsticker, K., M., Dorf., Fitzenberger,<br />

R., Bösch, H., Stimpfle, R.M., Wilmouth, D.M., Anderson, J.G., Richard, E.C., Fahey, D.W., &<br />

Gao, R.S.and Bui, T.P. 2005. Analysis of BrO, ClO, and nighttime OClO in the arctic winter<br />

stratosphere. J. Geophys. Res., 110, D01301, doi:10.1029-/2004JD005035.<br />

Dorf, M. 2005. Investigation of inorganic stratospheric bromine by balloon-borne DOAS measurements<br />

and model simulations. PhD thesis, University of Heidelberg, Heidelberg, Germany.<br />

Dufour, G., Payan, S., Lefévre, F., Berthet, G., Eremenko, M., Butz, A., Jeseck, P., Té, Y., Pfeilsticker,<br />

K., & Camy-Peyret, C. 2005. 4D comparison method to study the NOy partitioning in summer<br />

polar stratosphere: Influence of aerosol burden. Atmos. Chem. Phys., 5, 919 – 926.<br />

Hendrick, F., Barret, B., Van Roozendael, M., Boesch, H., Butz, A., De Mazière, M., Goutail, F.,<br />

Lambert, J.-C., Pfeilsticker, K., & Pommereau, J.P. 2004. Retrieval of nitrogen dioxide stratospheric<br />

profiles from ground-based zenith-sky UV-visible observations: Validation of the technique through<br />

correlative comparisons. Atmos. Chem. Phys., 4, 2867 – 2904.<br />

Organization), WMO (World Meteorological. 2003. Scientific Assessment of Ozone Depletion: 2002,<br />

Global Ozone Research and Monitoring. Geneva, Project Report No. 47, 498 pp.<br />

Reichl, U. 2005. Ground-based direct Sun UV/vis spectroscopy in Timon/Northeastern Brazil: Comparison<br />

of tropospheric air mass pollution in the dry and wet season. Diploma thesis, University of<br />

Heidelberg, Heidelberg, Germany.<br />

Schwärzle, J. 2005. Spektroskopische Messung von Halogenoxiden in der marinen atmosphärischen<br />

Grenzschicht in Alcântara/Brasilien. Staatsexamensarbeit, University of Heidelberg, Heidelberg,<br />

Germany.<br />

Vandaele, A.C., Fayt, C., Hendrick, F., Hermans, C., Humbled, F., Van Roozendael, M., Gil, M.,<br />

Navarro, M., Puentedura, O., Yela, M., Braathen, G., Stebel, K., Tornkvist, K., Johnston, P.,<br />

Kreher, K., Goutail, F., Mieville, A., Pommereau, J.-P., Khaikine, S., Richter, A., Oetjen, H.,<br />

Wittrock, F., Bugarski, S., Frieß, U., Pfeilsticker, K., Sinreich, R., Wagner, T., Corlett, G., &<br />

Leigh, R. 2005. An intercomparison campaign of ground-based UV-Visible measurements of NO2,<br />

BrO, and OClO slant columns. Methods of analysis and results for NO2. J. Geophys. Res., 110,<br />

D08305, doi:10.1029/2004JD005423.<br />

Weidner, F. 2005. Development and application of a versatile balloon-borne DOAS instrument for<br />

skylight radiance and atmospheric trace gas measurements. PhD thesis, University of Heidelberg,<br />

Heidelberg, Germany.<br />

Weidner, F., Bösch, H., Bovensmann, H., Burrows, J.P., Butz, A., Camy-Peyret, C., Dorf, M.,<br />

Gerilowski, K., Gurlit, W., Platt, U., von Friedeburg, C., Wagner, T., & Pfeilsticker, K. 2005.<br />

Balloon-borne limb profiling of UV/vis skylight radiances, O3, NO2, and BrO: Technical set-up<br />

and validation of the method. Atmos. Chem. Phys., 5, 1409 – 1422.


2.3. RADIATIVE TRANSFER 45<br />

2.3 Radiative Transfer<br />

Participating scientists Pfeilsticker, K., A. Butz, M. Dorf, A. Lindner, A. Lotter, U. Reichl, T.<br />

Scholl, and F. Weidner<br />

Abstract Research on the radiative transfer (RT) in the Earth’s atmosphere at the IUP concentrates<br />

on an improved understanding of the UV/vis solar irradiance, its temporal variation and the deposition<br />

of solar radiation in the atmosphere. These studies include spectroscopic measurements from different<br />

platforms and sophisticated radiative transfer modelling.<br />

Figure 2.19: Upper panel: Comparison of measured (black) and simulated (red) oxygen A-band<br />

spectrum for the observation at Cabauw (NL) on May 11, 2003 at UT 14:59. The identification of the<br />

oxygen A-band and solar Fraunhofer lines is given next to the line. Middle panel: Residual spectrum<br />

taken as the natural log of the ratio of measured and simulated spectra, hence the natural units of<br />

vertically-integrated optical density (VOD) airmass. Lower panel: Inferred photon path-<strong>pdf</strong>, assuming<br />

a Gamma-distribution for the in-cloud transfer (adopted from Scholl et al. [2005])<br />

Background The transfer of solar radiation in the Earth’s atmosphere is one of the most complicated<br />

issues in environmental sciences, mostly owing due to the variety and complicated nature<br />

of atmospheric absorbers and scatters (e.g., gases, aerosols, liquid and solid cloud particles), their<br />

spectroscopic signatures and varying spatial arrangements. Accordingly it is found that, e.g., clear<br />

and cloudy sky RT is the major uncertainty in climate modelling and the validation of RT codes<br />

thus appears to be necessary. Also, RT codes find applications in photochemical investigations and<br />

in in-situ and remote sensing studies.<br />

Scientific objectives of radiative transfer studies include the following<br />

• the measurements of photon path length distributions of solar photons being transmitted to the<br />

ground (see 2.3.2)


46 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

• the absolute spectral solar irradiance (320 - 650 nm) and its temporal variation (see 2.3.3)<br />

• the measurement of UV/visible actinic fluxes (e.g., of JNO2) and of the limb radiance near<br />

horizon<br />

• the detection and characterization of unknown, overlooked, or yet poorly characterized atmospheric<br />

absorbers, such as the H2O continuum absorption, meta-stable and stable H2O − H2O<br />

dimers, or the collisional complex O2 − O2, .... (see 2.3.4)<br />

• the measurements of the stratospheric aerosol extinction and its relation to volcanic eruptions.<br />

• the validation of level 1 products (spectral solar irradiance, and limb radiances) of the SCIA-<br />

MACHY instrument deployed on the European research satellite ENVISAT (see 2.3.1).<br />

Arguably all these activities aim at a better understanding of the primary driving force of the<br />

climate system e.g., the solar radiation and its deposition in Earth’s atmosphere. The research thus<br />

contributes to better quantify and assess man’s impact on the past, present and future global climate.<br />

Methods used for the investigations of the radiative transfer involve (1) spectroscopic measurements<br />

of the absolute spectral solar irradiance in the UV/vis/near-IR and of corresponding near horizon<br />

skylight limb radiances from different spectrometers (grating and Fourier-Transform) deployed on<br />

high altitude (∼ 40 km) balloon platforms including on-side absolute radiometric calibration to NIST<br />

(National <strong>Institut</strong>e of Standard and Technology, USA) and PTB (Physikalische Technische Bundesanstalt)<br />

radiometric standards (2) ground-based high spectral resolution spectroscopic measurements<br />

of zenith scattered skylight around the oxygen A-band (767 - 771 nm) (see Figure 2.19, upper panel),<br />

that aim at the detection of photon path length distribution of solar photons for a variety of cloudy<br />

skies (see Figure 2.19, lower panel) and (3) long-path spectroscopic absorption measurements near<br />

surface in wavelength intervals ranging from the UV to the near-IR. All the different instruments<br />

are deployed on internationally organized field campaigns that address a wider range of scientific<br />

objectives (see below). The interpretation of these measurements also involves sophisticated radiative<br />

transfer modelling (ray-tracing, Monte Carlo, discrete ordinate models, DISORT) that e.g., account<br />

for the sphericity of the atmosphere, refraction, time and space dependent trace gas and aerosol<br />

concentrations and cloud cover. Activity (1) is performed within a French/German collaboration with<br />

the Laboratoire de Physique Moléculaire et Applications, Université Pierre et Marie Curie, Paris,<br />

France and (2) within a collaboration with the IUP at the University of Bremen, Germany.<br />

Field Campaigns & Studies<br />

1. March 04: a high latitude balloon campaign at Kiruna/Sweden (67.9 o N, 21.2 o W) within the<br />

ENVISAT/SCIAMACHY validation<br />

2. Nov./Dec./Jan. 2004/05: a tropical balloon campaign at Teresina/Brazil (5.1 o S, 42.9 o W) within<br />

the ENVISAT/SCIAMACHY validation and at Alcantara/Sao Luis/Brazil (2.39 o S, 44.38 o W).<br />

3. June 2005: a tropical balloon campaign at Teresina/Brazil (5.1 o S, 42.9 o W) within the EN-<br />

VISAT/SCIAMACHY validation<br />

International Cooperation The research group closely cooperates with the following institutions<br />

as, e.g., documented in joint peer-review publications.<br />

(1) Laboratoire de Physique Moléculaire pour l’Atmosphere et l’Astrophysique (LPMAA), Université<br />

Pierre et Marie Curie, Paris, France, (2) Meteorologisches <strong>Institut</strong>, Freie <strong>Universität</strong> Berlin, Berlin,<br />

Germany, (3) European Space Agency (ESA), Nordwijk, The Netherlands, (4) <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong><br />

und Fernerkundung, University of Bremen, Bremen, Germany, (5) Los Alamos National Laboratory,<br />

Space and Remote Sensing Sciences Group, Los Alamos, USA, (6) Royal Netherlands Meteorological<br />

<strong>Institut</strong>e (KNMI), De Bilt, The Netherlands, (7) Meteorological <strong>Institut</strong>e, University of<br />

Bonn, Bonn, Germany, (8) Meteorological <strong>Institut</strong>e, University of Munich, Munich, Germany, (9)<br />

GKSS Research Centre, Geesthacht, Germany.<br />

Future work will concentrate on studies (1) of the inter annual variation of the spectral solar<br />

irradiance and its relation to climate change, (2) improved measurements of path length distribution<br />

of solar photons during the life-time of cloud systems, (3) high resolution spectroscopic studies of the<br />

visible and near-IR spectrum of water vapor and (4) 2-D imaging spectroscopy of radiative properties<br />

of the atmosphere.


2.3. RADIATIVE TRANSFER 47<br />

Funding comes through research contracts with the BundesMinisteriumForschungs&Technologie<br />

(BMBF), through the DLR (DLR-50FE0017) and GSF (GSF-07ATF24) and the Deutsche Forschungsgemeinschaft<br />

(DFG PF384/2-1 and PF384/2-3).<br />

Publications<br />

Peer reviewed publications:<br />

1. Crewell et al. [2004]<br />

2. Gurlit et al. [2005]<br />

3. Scholl et al. [2005]<br />

4. Weidner et al. [2005]<br />

PhD theses:<br />

1. Weidner [2005]<br />

Diploma theses:<br />

1. Lindner [2005]<br />

Invited Talks<br />

1. Pfeilsticker et al. [2004]<br />

2. Pfeilsticker [2005a]<br />

3. Pfeilsticker [2005b]


48 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

2.3.1 Development and Application of a Versatile Balloon-Borne DOAS<br />

Instrument for Skylight Radiance and Atmospheric Trace Gas Profile<br />

Measurements<br />

Participating scientists Weidner, F., H. Bösch, A. Butz, M. Dorf, U. Platt, C. von Friedeburg,<br />

T. Wagner, and K. Pfeilsticker<br />

Abstract A novel balloon-borne UV/vis DOAS instrument measuring limb scattered radiation was<br />

developed, characterized in the laboratory and employed during 5 stratospheric balloon flights. Skylight<br />

radiance and concentration profiles of O3, NO2, and BrO are retrieved and compared to radiative<br />

transfer simulations and measurements of the same parameters.<br />

Background In the past two decades remote<br />

sensing of the atmosphere by optical methods<br />

has evolved into a powerful tool for meteorology,<br />

atmospheric photochemistry and climate studies.<br />

Most recently, space-borne UV/vis limb observations<br />

have also become available, e.g., through<br />

the SME, SOLSE/LORE, Odin/OSIRIS, and EN-<br />

VISAT/SCIAMACHY instruments. Quasi in-situ<br />

UV/vis limb profiling from balloon may also offer<br />

a new method for time resolved spectroscopy of<br />

ozone harmful radicals in the stratosphere.<br />

Scientific questions that can be tackled by<br />

UV/vis limb measurements are:<br />

(1) measurements of near horizon limb radiance<br />

for different illumination conditions and validation<br />

of radiative transfer codes.<br />

(2) Monitoring profiles of stratospheric radical<br />

species, such as O3, NO2, BrO, OClO, IO, ....<br />

and studies of their photochemistry and budget,<br />

e.g., for the systems NO2/N2O5 (see 2.2.3) or<br />

BrO/OClO and its importance for ozone loss.<br />

Methods UV/visible skylight radiances (330 −<br />

550 nm) are measured from azimuth controlled<br />

balloon payloads which are flying into the middle<br />

stratosphere (∼ 32km). The spectra are analyzed<br />

for along-the-sights column densities of O3,<br />

NO2, BrO, H2O, and O4 by Differential Optical<br />

Absorption Spectroscopy (DOAS). Radiative<br />

Transfer (RT) calculations, e.g., with the lab programmed<br />

Monte Carlo RT Model TRACY, are<br />

used to (a) simulate the measured quantities and<br />

(b) infer vertical profiles of O3, NO2, BrO and<br />

OClO concentrations using the Maximum a Posteriori<br />

(MAP) inversion technique. Subsequent<br />

measurements of the profiles of these species allow<br />

us to draw information on the temporal or<br />

spatial variations (or both) of these species and<br />

the related photochemistry.<br />

Results Balloon-borne UV/vis limb scattered<br />

measurements is tested against simultaneous measurements<br />

of the same parameters available from<br />

in-situ, or UV/vis/near IR solar occultation observations<br />

performed on the same payload. Reasonable<br />

agreement is found between (a) measured and<br />

RT calculated limb radiances and (b) inferred limb<br />

O3, NO2, and BrO (see Figure 2.20) and correlative<br />

profile measurements when properly accounting<br />

for all relevant atmospheric parameters (temperature,<br />

pressure, aerosol extinction, and major<br />

absorbing trace gases).<br />

Figure 2.20: Comparison of retrieved BrO profiles<br />

from mini-DOAS limb measurements (black line)<br />

and direct sunlight DOAS measurements (red<br />

line) during balloon ascent for an LPMA/DOAS<br />

balloon flight in Kiruna, March 24 th , 2004 with a<br />

priori profile in green.<br />

Additionally, scanning limb observations provide<br />

time-resolved profile information of radicals<br />

during sunset.<br />

Future work should concentrate on the application<br />

of the method on photochemical studies addressing<br />

the loss in stratospheric ozone at high,<br />

middle, and low latitudes, including the tropical<br />

tropopause region.<br />

Main publication Weidner, F., Development<br />

and Application of a Versatile Balloon-Borne<br />

DOAS Instrument for Skylight Radiance and Atmospheric<br />

Trace Gas Profile Measurements, Ph.D.<br />

thesis, <strong>Universität</strong> Heidelberg, Heidelberg, 2005.


2.3. RADIATIVE TRANSFER 49<br />

2.3.2 Oxygen A-band measurements for solar photon path length distribution<br />

studies<br />

Participating scientists Scholl, T., and K. Pfeilsticker<br />

Abstract High resolution spectroscopy of the oxygen A-band (760-780 nm) in zenith scattered<br />

skylight is a powerful tool to infer path length distributions (PDF) of solar photons transmitted to<br />

the ground. The relation between the different moments of the PDF (〈L〉, 〈L 2 〉) and the rescaled<br />

cloud optical depth τ ∗ is a strong indicator for 3D-effects on the radiative transfer (RT).<br />

Height [m]<br />

10000<br />

8000<br />

6000<br />

4000<br />

2000<br />

0 :0<br />

12:<br />

:5 :10 :15 :20 :25 :30 :35 :40 :45 :50 :55<br />

Time [UTC]<br />

-60 -50 -40 -30 -20 -10 0 10 20<br />

Reflectivity [dBZ]<br />

Figure 2.21: left panel: Measured radar reflectivities from KNMI 35 GHz Radar for May 22, 2003 UT 12:00-<br />

13:00, right panel: Mean cloud photon paths 〈Lc〉 as a function of effective cloud optical depth τ ∗ c . The black<br />

lines are predictions for different values of the Lévy exponent α ≤ 2. The 3 data clusters (color-coded blue,<br />

red and green) correspond to the 3 different probed cloud situations.<br />

Background Modelling RT in cloudy skies is<br />

one of the most challenging tasks in climate modelling.<br />

Photon PDF is commonly a hidden property<br />

of standard RT models, controlled by the<br />

spatial distribution of scattering and absorption.<br />

The distribution in the near infrared region is<br />

very representative for the shortwave region as<br />

a whole. The principle of equivalence allows to<br />

draw conclusions about radiative properties of<br />

the atmosphere from a photon PDF measured in<br />

one wavelength band, since the scattering properties<br />

of clouds and aerosols vary slowly and predictably<br />

with wavelength. Here the first two moments<br />

of the photon PDF of solar photons transmitted<br />

through cloudy skies to the ground are<br />

investigated. Combining the spectroscopic measurements<br />

with other cloud properties measured<br />

simultaneously by in-situ techniques during two<br />

campaigns allows to test the theory of anomalous<br />

photon diffusion through clouds.<br />

Methods and Results The multiple of different<br />

line strengths offered by the oxygen A-band<br />

implicitly provide direct information on the PDF<br />

of the photons transmitted to the ground. The<br />

spectral retrieval is solved by forward modelling<br />

the measured spectra with a prescribed photon<br />

PDF (usually a Γ function) at high spectral resolution.<br />

The free parameters of the PDF are<br />

then iteratively calculated by using a Nonlinear<br />

Least Square Fit leading to the searched quantities<br />

〈L〉 and 〈L 2 〉. Davis & Marshak [2002]<br />

inferred for the first moment of photon PDF:<br />

〈Lc〉/∆H = (1/2 · [1 + C(ɛ)] · τ ∗ ) α−1 . α is the so<br />

called Lévy index which ranges between 1 and 2.<br />

In particular, the value α = 2 is attained for a homogenous<br />

slab and for α < 2 for inhomogeneous<br />

slab. In Figure 2.21 the enhancement of the mean<br />

photon path length in the cloud (as a function of<br />

τ ∗ = τ · (1 − g)) and the received Lévy index is<br />

shown.<br />

The findings confirm the theory of anomalous<br />

photon diffusion through clouds and the predictions<br />

for the values in the path length to optical<br />

depth relations. It also provides further evidence<br />

that cloudy sky photon path length require consideration<br />

of non-classical photon transport theory.<br />

Funding comes through the AFO-2000 4D<br />

Clouds project (BMBF-07ATF24).<br />

Outlook Photon PDFs are a central concept of<br />

cloud RT modelling. For further improvements<br />

imaging DOAS spectroscopy at high temporal and<br />

spatial resolution is required.<br />

Main publication Scholl, T., Photon path<br />

length distributions for cloudy skies: Their first<br />

and second-order moments inferred from high resolution<br />

oxygen A-Band spectroscopy, PhD-Thesis,<br />

<strong>Universität</strong> Heidelberg, Heidelberg, in preparation.


50 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

2.3.3 Absolutely calibrated solar irradiance measurements<br />

Participating scientists Lindner, A., H. Bösch, A. Butz, M. Dorf, F. Weidner, and K. Pfeilsticker<br />

Abstract Absolutely calibrated solar irradiance spectra are measured from aboard the LPMA/<br />

DOAS balloon gondola at around 30 to 35 km altitude. After accounting for residual atmospheric extinction<br />

the findings are compared to previous observations and discussed with respect to implications<br />

for atmospheric photochemistry and the Earth’s climate.<br />

Figure 2.22: Ratio of solar irradiance spectra referenced to the solar spectrum of Kurucz et al. [1984] with<br />

recent updates of Fontenla et al. [1999] (MODTRAN 3.7) with (a) the present balloon borne measurement,<br />

(b) SORCE/SIM Harder et al. [2000], (c) SCIAMACHY/ENVISAT in channel 1, 2, 3, and 4 using the revised<br />

IUP-Bremen calibration.<br />

Background Solar radiation is the driving force<br />

for climate and thus for life on Earth. Evidently,<br />

the extraterrestrial solar irradiance Eo and its<br />

temporal evolution is of primary interest for atmospheric<br />

spectroscopy, photochemistry, climate<br />

and the solar cell industry as well. Although Eo is<br />

monitored by a large number of space-borne, airborne<br />

and ground-based instruments, to date, a<br />

consensus on Eo could only be achieved within few<br />

percents in the UV-A and visible spectral wavelength<br />

ranges mainly due to given problems with<br />

the absolute calibration of the radiation measurements<br />

and long term drifts of the various sensors.<br />

Funding The present work has been supported<br />

by ESA, BMBF, DLR and the European Union.<br />

Methods and results Here, direct Sun observations<br />

from aboard the LPMA/DOAS balloon<br />

payload are used to absolutely infer Eo in<br />

two wavelength bands in the UV/visible spectral<br />

range. After an on-ground spectro-radiometrical<br />

calibration has been performed for each balloon<br />

flight, the solar irradiance measurements are conducted<br />

at about 30 to 35 km balloon float altitude<br />

where the remaining atmospheric extinction<br />

is minimal and can be accounted for easily. Thorough<br />

tracking and removal of systematic errors<br />

results in high-accuracy measurement of the extraterrestrial<br />

solar irradiance.<br />

Comparison of our balloon borne data set with<br />

previous studies yields excellent agreement, see<br />

Figure 2.22, and suggests that, to date, the integrated<br />

Eo is uncertain by as much as 5 W/m 2<br />

in the respective wavelength range Gurlit et al.<br />

[2005].<br />

Outlook/Future work<br />

• Quality check of the standard Eo recommendation<br />

by further refinement of the calibration<br />

procedure<br />

• Long term validation, monitoring and recalibration<br />

of satellite-borne Eo measurements<br />

• Monitoring of natural solar variability<br />

Main publications Lindner A., Ballongestütze<br />

Messungen der extraterrestrischen spektralen solaren<br />

Irradianz, Diploma thesis, University of Heidelberg,<br />

Germany, 2005.


2.3. RADIATIVE TRANSFER 51<br />

2.3.4 Atmospheric detection of water dimers and their contribution to<br />

solar shortwave absorption<br />

Participating scientists Lotter, A., C . Peters, J. Schwärzle, and K. Pfeilsticker<br />

Abstract The cause of the water vapor continuum and possible contributions to it by water dimers<br />

is one of the most challenging question in atmospheric spectroscopy. Field measurements by means<br />

of active long-path differential optical absorption spectroscopy (DOAS) were performed to probe the<br />

atmosphere for water vapor continuum and dimer absorption.<br />

Figure 2.23: Absorption cross section for water monomer (WM) and water dimer (WD). Due to the overlap,<br />

WD absorption is masked by strong WM absorption, except for the three marked regions, where detection<br />

may be possible.<br />

Background Disagreement in Earth’s radiation<br />

budget between observations and radiative transfer<br />

models has been a major concern for several<br />

decades, as there exists a significant level of solar<br />

shortwave (SW) cloudy-sky absorption, commonly<br />

referred to as excess absorption, beyond the<br />

ability of any model to predict. Many attempts<br />

have been made to explain the observed excess of<br />

solar SW absorption, but all potential mechanisms<br />

on their own fall far short of explaining a possible<br />

absorption deficit as much as 30 W/m 2 . One<br />

mechanism of the required additional absorption<br />

was suggested to come from a combined contribution<br />

of the water continuum and water dimers<br />

(WD). WDs may also play an important role in atmospheric<br />

physics by e.g., initiating homogeneous<br />

nucleation of water and photo-chemistry by catalyzing<br />

chemical reactions (e.g., in the formation<br />

of H2SO4).<br />

Methods Possible atmospheric WD absorption<br />

was investigated by extreme long path (up to<br />

29 km) near ocean surface absorption measurements<br />

during 3 field campaigns conducted in<br />

Northern Germany in May 2002, France in June<br />

2003, tropical Brazil in Dec./Jan. 2004. Since the<br />

near-IR absorption spectrum of WD is predicted<br />

to largely overlap with that of WM, 3 almost interference<br />

free WD lines were selected for the study<br />

(see Figure 2.23). Here, the dependance of WD<br />

absorption on the WM pressure squared is used<br />

as an indicator for WD detection.<br />

Results Although a WD absorption line at<br />

13340 cm −1 was tentatively identified to be due to<br />

WD absorption (Pfeilsticker et al. [2003]), subsequent<br />

campaigns involving a larger WM concentration<br />

(e.g., in Brazil) could not confirm its existence.<br />

However, the latter measurements indicate<br />

a possible WD absorption band at 16312 cm −1 .<br />

Uncertainties, however, still remain in WD identification<br />

due to uncertainties in the predicted WD<br />

line position (up to 200 cm −1 ) and width (10–<br />

200 cm −1 FWHM). The latter being a function<br />

as to whether WD are truly bound, meta-stable<br />

or simply free pair states. WD detection is also<br />

hindered by uncertainties in the WM data bases<br />

in particular for the WM weak lines.<br />

Funding comes through the Deutsche ForschungsGemeinschaft<br />

(PF 384/1-2 and 2-3).<br />

Outlook More sensitive detection of WD absorption<br />

will require higher quality WM and WD<br />

data than existing.<br />

Main publication Lotter A., Field measurements<br />

of water continuum and water dimer absorption<br />

by active long-path Differential Optical<br />

Absorption Spectroscopy (DOAS), PhD thesis,<br />

<strong>Universität</strong> Heidelberg, Heidelberg, Germany, in<br />

preparation.


52 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

References<br />

Coheur, P.-F., Fally, S., Carleer, M., Clerbaux, C., Colin, R., Jenouvrier, A., Mérienne, M.-F., Hermans,<br />

C., & Vandaele, A. C. 2002. New water vapor line parameters in the 26000 - 13000 cm −1<br />

region. J. Quant. Spec. and Rad. Transf., 74, 493 – 510.<br />

Crewell, S., Bloemink, H., Feijt, A., García, S.G., Jolivet, D., Krasnov, O.A., van Lammeren, A.,<br />

Löhnert, U., van Meijgaard, E., Meywerk, J., Quante, M., Pfeilsticker, K., Schmidt, S., Scholl, T.,<br />

Simmer, C., Schröder, M., Trautmann, T., Venema, V., Wendisch, M., & Willén, U. 2004. The<br />

BALTEX Bridge Campaign - An integrated approach for a better understanding of clouds. Bull.<br />

Am. Met. Soc., 85, 1565 – 1584.<br />

Davis, A. B., & Marshak, A. 2002. Space-time characteristics of light transmitted by dense clouds: A<br />

Green function analysis. J. Atmos. Sci., 59, 2713 – 2727.<br />

Fally, S., Coheur, P.-F., Carleer, M., Clerbaux, C., Colin, R., Jenouvrier, A., Mérienne, M.-F., Hermans,<br />

C., & Vandaele, A. C. 2003. Water vapor line broadening and shifting by air in the 26000 -<br />

13000 cm −1 region. J. Quant. Spec. and Rad. Transf., 82, 119 – 131.<br />

Fontenla, J., White, O. R., Fox, P. A., Avrett, E. H., & Kurucz, R. L. 1999. Calculation of solar<br />

irradiances, I. Synthesis of the solar spectrum. Astrophys. J., 518, 480 – 500.<br />

Gurlit, W., Bösch, H., Bovensmann, H., Burrows, J. P., Butz, A., Camy-Peyret, C., Dorf, M., Gerilowski,<br />

K., Lindner, A., Noël, S., Platt, U., Weidner, F., & Pfeilsticker, K. 2005. The UV-A<br />

and visible solar irradiance spectrum: Inter-comparison of absolutely calibrated, spectrally medium<br />

resolved solar irradiance spectra from balloon-, and satellite-borne measurements. Atmos. Chem.<br />

Phys., 5, 1879 – 1890.<br />

Harder, J., Lawrence, G., Rottman, G., & Woods, T. 2000. The Spectral Irradiance Monitor (SIM)<br />

for the SORCE Mission. Proc. SPIE, 4135, 204 – 214.<br />

Kurucz, R. L., Furenlid, I., Brault, J., & Testerman, L. 1984. Solar Flux Atlas from 296 to 1300 nm.<br />

National Solar Observatory, Atlas No. 1. ftp://ftp.noao.edu/fts/fluxatl.<br />

Lindner, A. 2005. Ballongestütze Messungen der extraterrestrischen spektralen solaren Irradianz.<br />

Diploma thesis, University of Heidelberg, Heidelberg, Germany.<br />

Partridge, H., & Schwenke, D. W. 1997. The determination of an accurate isotope dependent potential<br />

energy surface for water from extensive ab initio calculations and experimental data. J. Chem. Phys.,<br />

106, 4618 – 4639.<br />

Pfeilsticker, K. 2005a. Collisional complexes, metastable, and stable complexes in the atmosphere, and<br />

their potential importance for the absorption of solar radiation. Gordon Research Conference on<br />

Radiation & Climate, Colby College, Waterville, ME, USA, July 24-29.<br />

Pfeilsticker, K. 2005b. Recent cloudy sky photon path <strong>pdf</strong> measurements from Heidelberg. 3rd I3RC<br />

Workshop, IFM Kiel, October 11-14.<br />

Pfeilsticker, K., Lotter, A., Peters, C., & Bösch, H. 2003. Atmospheric detection of water dimer via<br />

near-infrared absorption. Science, 300, 2078 – 2080.<br />

Pfeilsticker, K., Lotter, A., Boesch, H., & Peters, C. 2004. Collisional complexes, metastable and stable<br />

dimers in the atmosphere, and their potential importance for the absorption of solar radiation. 228th<br />

National ACS Meeting, Philadelphia, PA, USA, August 22-26.<br />

Rothman, L. S., Barbe, A., Benner, D. C., Brown, L. R., Camy-Peyret, C., Carleer, M. R., Chance,<br />

K., Clerbaux, C., Dana, V., Devi, V. M., Fayt, A., Flaud, J.-M., Gamache, R. R., Goldman, A.,<br />

Jacquemart, D., Jucks, K. W., Lafferty, W. J., Mandin, J.-Y., Massie, S. T., Nemtchinov, V.,<br />

Newnham, D. A., Perrin, A., Rinsland, C. P., Schroeder, J., Smith, K. M., Smith, M. A. H., Tang,<br />

K., Toth, R. A., Vander Auwera, J., Varanasi, P., & Yoshino, K. 2003. The HITRAN molecular<br />

spectroscopic database: edition of 2000 including updates through 2001. J. Quant. Spec. and Rad.<br />

Transf., 82, 5 – 44.


2.3. RADIATIVE TRANSFER 53<br />

Rothman, L. S., Jacquemart, D., Barbe, A., Benner, D. C., Birk, M., Brown, L. R., Carleer, M. R.,<br />

Chackerian Jr., C., Chance, K., Coudert, L. H., Dana, V., Devi, V. M., Flaud, J.-M., Gamache,<br />

R. R., Goldman, A., Hartmann, J.-M., Jucks, K. W., Maki, A. G., Mandin, J.-Y., Massie, S. T.,<br />

Orphal, J., Perrin, A., Rinsland, C. P., Smith, M. A. H., Tennyson, J., Tolchenov, R. N., Toth, R. A.,<br />

Vander Auwera, J., Varanasi, P., & Wagner, G. 2005. The HITRAN 2004 molecular spectroscopic<br />

database. J. Quant. Spec. and Rad. Transf., 96, 139 – 204.<br />

Scholl, T., Pfeilsticker, K., Davis, A.B., Klein Baltink, H., Crewell, S., Löhnert, U., Simmer, C.,<br />

Meywerk, J., & Quante, M. 2005. Path length distributions for solar photons under cloudy skies:<br />

Comparison of measured first and second moments with predictions from classical and anomalous<br />

diffusion theories. J. Geophys. Res., revised.<br />

Weidner, F. 2005. Development and application of a versatile balloon-borne DOAS instrument for<br />

skylight radiance and atmospheric trace gas measurements. PhD thesis, University of Heidelberg,<br />

Heidelberg, Germany.<br />

Weidner, F., Bösch, H., Bovensmann, H., Burrows, J.P., Butz, A., Camy-Peyret, C., Dorf, M.,<br />

Gerilowski, K., Gurlit, W., Platt, U., von Friedeburg, C., Wagner, T., & Pfeilsticker, K. 2005.<br />

Balloon-borne limb profiling of UV/vis skylight radiances, O3, NO2, and BrO: Technical set-up<br />

and validation of the method. Atmos. Chem. Phys., 5, 1409 – 1422.


2.4. DOAS TOMOGRAPHY GROUP 55<br />

2.4 DOAS Tomography Group<br />

Group members<br />

Dr. Irene Pundt, head of group<br />

Dipl. Met. Claudia Hak, PhD student<br />

Dipl. Phys. Andreas Hartl, PhD student<br />

Dipl. Phys. Klaus-Peter Heue, PhD student<br />

Dipl. Phys. Kai-Uwe Mettendorf, PhD student<br />

MPhys. Denis Pöhler, PhD student<br />

Bing-Chao Song, Research assistant<br />

Alexander Stelzer, Diploma Student<br />

Abstract The DOAS tomography group is a junior research group of the BMBF atmospheric research<br />

program 2000 (AFO 2000). The group started in August 2000 as part of the research group<br />

Atmospheric Physics of Prof. Dr. Ulrich Platt. DOAS Tomography is a novel technique developed<br />

for spatially resolved measurements of trace gas distributions. In the framework of the Tom-DOAS<br />

project, first tomographic measurements from ground and aircraft were carried out. New instruments<br />

were developed and the method was validated during an indoor campaign. In addition computer tools<br />

were developed to optimise instrumental configurations and to invert the measurements. The quality<br />

of the localization and quantification of atmospheric emission plumes was estimated by numerical<br />

studies.<br />

Figure 2.24: Left: Groundbased tomographic setup using Longpath DOAS instruments. From each<br />

telescope (houses) light beams are directed towards the four retro reflector arrays (yellow circles). The<br />

light travels back to the initial telescopes, where it is spectrally analysed. Right: Airborne tomographic<br />

measurements. Here the sunlight is captured by several telescopes from different directions. Using<br />

measurements from different aircraft positions, a large number of intersecting light paths can be<br />

achieved. The resulting trace gas column densities are subsequently inverted to obtain 2D-distributions<br />

of trace gas concentrations.<br />

Overarching topic and Background<br />

Air pollution due to anthropogenic trace gas emissions can cause serious environmental and medical<br />

problems. For example, for human beings air pollutants like ozone, nitrogen dioxide (NO2), sulphur<br />

dioxide (SO2) and benzene cause respiratory diseases. The predictability of their spatial distributions<br />

is subject to numerous uncertainties. For continuous concentration records some wide meshed networks<br />

of in situ measurement stations were installed. However, single-point measurements are often not<br />

sufficient in order to explain differences between models since small-scale characteristics of the models<br />

are not taken into account. In contrast, spatially resolved measurements can provide this type of<br />

information.<br />

Differential optical absorption spectroscopy (DOAS) is a path-integrating measurement technique<br />

for atmospheric trace gases like ozone, nitrogen oxides, SO2, halogen oxides (BrO, IO, OClO) and many<br />

hydrocarbons. For DOAS, a continuous artificial or natural light source (sun, moon, ) is used. Because<br />

of the characteristic absorption features it is possible to measure several trace gases simultaneously<br />

(e.g. NO2, SO2, HCHO, HONO, and ozone in the UV region). In a typical so-called long-path (LP)<br />

setup a beam of white light, emitted by a telescope, travels through the atmosphere to a retro-reflector<br />

and back to the telescope. Absorption patterns in the received light allow determining the column<br />

density (the integrated concentration) of the trace gases along the light path.<br />

Our DOAS tomography setups consist of a number of intersecting light paths (left figure). Column<br />

densities of one or several trace gases measured by the DOAS technique along the light paths are


56 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

inverted to obtain concentration distributions by tomographic techniques.<br />

In contrast, the Airborne Multi AXis (AMAX) DOAS instrument measures passively the sunlight<br />

which is scattered in the earths atmosphere and/or reflected on the ground (right figure). Several small<br />

telescopes are used which are directed in various directions and which capture the light simultaneously.<br />

Each measurement provides results from several different paths throughout the atmosphere. As the<br />

aircraft moves on from measurement to measurement, data of many intersecting light paths is recorded.<br />

First tomographic line-integrating indoor measurements of 2D trace gas distributions were realized<br />

in the 1990s by using open-path Fourier infrared absorption spectroscopy. There have been improvements<br />

in speed and spatial resolution since, but all experiments have been restricted to the laboratory<br />

environment so far.<br />

Main methods<br />

During the last five years, for the first time DOAS two-dimensional tomographic experiments using a<br />

larger number (10-90) of intersecting light paths have been carried out (e.g., Pundt [2005b]). At the<br />

ground, long path active instruments were used to measure 2D emission plumes from road traffic or<br />

horizontal distributions of trace gases (e.g. Pundt et al. [2005c], Lösch [2001], Kunz [2001], Bäuerle<br />

[2004], Rippel [2005], Poehler et al. [2005]). Instruments which are more suitable for tomographic<br />

applications were developed (Pundt & Mettendorf [2005], Mettendorf [2005]) and the reconstruction<br />

methods were validated during an indoor campaign (Mettendorf et al. [2005]). From aircraft, passive<br />

instruments were used to measure 2D distributions of a power plant emission plume (Pundt et al.<br />

[2005a], Heue et al. [2005]). The quality of the localization and quantification of atmospheric emission<br />

plumes has been estimated by means of numerical studies (Knab [2004], Laepple et al. [2004], Hartl<br />

et al. [2005a]). In addition, the group participated in two measurement campaigns in the Po-Valley<br />

region in the framework of the EU FORMAT project (e.g., Hak et al. [2005]).<br />

Subprojects<br />

Groundbased DOAS tomography<br />

Airborne DOAS tomography<br />

Theoretical studies<br />

FORMAT: Formaldehyde as a Tracer of Photo oxidation in the Troposphere (EU project)<br />

Funding<br />

BMBF (TomDOAS)<br />

EU (FORMAT)<br />

Cooperation<br />

University of Bremen<br />

FZK <strong>Karls</strong>ruhe (IMK <strong>Karls</strong>ruhe)<br />

IFU Garmisch-Partenkirchen (IMK <strong>Karls</strong>ruhe)<br />

NILU (Norway)<br />

IASB (Belgium)<br />

PSI (Switzerland)<br />

Anhui <strong>Institut</strong>e (Hefei, China)<br />

Publications<br />

Peer reviewed Publications<br />

1. Bruns et al. [2004]<br />

2. Fix et al. [2005]<br />

3. Hak et al. [2005]<br />

4. Heckel et al. [2005]<br />

5. Heue et al. [2005]<br />

6. Laepple et al. [2004]<br />

7. Pundt & Mettendorf [2005]


2.4. DOAS TOMOGRAPHY GROUP 57<br />

8. Pundt [2005b]<br />

9. Pundt et al. [2005c]<br />

10. von Friedeburg et al. [2005]<br />

11. Wang et al. [2005b]<br />

Other Publications<br />

1. Bruns et al. [2005]<br />

2. Hartl et al. [2005b]<br />

3. Hartl et al. [2005a]<br />

4. Heue et al. [2004]<br />

5. Poehler et al. [2005]<br />

6. Pundt et al. [2005b]<br />

7. Wang et al. [2005a]<br />

Doctoral Thesis<br />

1. Heue [2005]<br />

2. Mettendorf [2005]<br />

Diploma Thesis<br />

1. Stelzer [2005]<br />

2. Rippel [2005]<br />

3. Knab [2004]<br />

4. Bäuerle [2004]<br />

Invited talks<br />

1. Pundt [2005a]<br />

2. I. et al. [2005]


58 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

2.4.1 Intercomparison of ambient in-situ Formaldehyde Measurements in<br />

urban Air<br />

Participating scientist Claudia Hak et al.<br />

Abstract An intercomparison of in-situ formaldehyde (CH2O) measurements, including four different<br />

techniques, is presented. Formaldehyde levels between 1 and 13 ppbv were measured in an urban<br />

environment in Milano, Italy. By using only point measurement methods, it was ensured that all<br />

instruments probed the same air volume.<br />

Figure 2.25: Fractional difference histograms, calculated relative to a reference Hantzsch instrument<br />

Background Previous intercomparisons revealed<br />

significant disagreement among the techniques<br />

used. However, there was no general pattern<br />

in the deviations. Since formaldehyde is an<br />

important intermediate in the oxidation of VOCs<br />

and a source of HOx radicals, it was a major<br />

objective of the FORMAT (FORMAldehyde as<br />

a Tracer of photooxidation in the troposphere)<br />

project to intercompare the different available<br />

measurement techniques. These involved the wet<br />

chemical Hantzsch method (five instruments), the<br />

DNPH method with HPLC separation, DOAS<br />

and FTIR. For the optical methods DOAS and<br />

FTIR, White-multireflection systems were used.<br />

In contrast to long path integrating optical methods<br />

which average horizontally and vertically,<br />

they measure the absorption of trace gases along<br />

a short base path of a few metres.<br />

Funding FORMAT, European Union<br />

Methods and results Two methods were applied<br />

for the intercomparison of the measurement<br />

results. Firstly, an orthogonal regression analysis<br />

was performed, comparing the individual results<br />

of all instrument pairs with each other. The<br />

correlation analysis showed a very good agreement<br />

among the Hantzsch results, however the<br />

slopes and intercepts from the regression analysis<br />

revealed some systematic differences. The optical<br />

techniques showed larger scattering. The second<br />

method was the analysis of fractional differ-<br />

ences, i.e. the difference between the results of<br />

each instrument and an (arbitrarily chosen) reference<br />

instrument according to δ=([CH2O]instr.-<br />

[CH2O]ref.)/[CH2O]ref.. Because of its long and<br />

continuous time series, the BUW Hantzsch results<br />

were chosen as the reference. The figure depicts<br />

the results of the fractional difference analysis.<br />

The nearly collocation of mode, median and average<br />

for most distributions suggests symmetry<br />

in the distribution and therefore mostly random<br />

differences. In summary, a ±11% agreement was<br />

found among the Hantzsch results. The observed<br />

discrepancies were partly attributed to different<br />

calibration standards. The agreement of the two<br />

optical methods was within 5%, which is within<br />

the uncertainties of the UV and IR absorption<br />

cross-sections (both 5%). Hantzsch and spectroscopic<br />

techniques agreed within 15%. DNPH results<br />

were generally lower than the measurements<br />

of the continuous techniques by up to 25%. A<br />

more detailed description of the methods as well<br />

as the discussion of the problems and the uncertainties<br />

of the Hantzsch and the optical methods<br />

can be found in Hak et al. [2005].<br />

Outlook/Future work This work is finished.<br />

The discrepancies in liquid calibration standards<br />

of Hantzsch instruments form a task which is currently<br />

under investigation by other groups.<br />

Main publication Hak et al. [2005]


2.4. DOAS TOMOGRAPHY GROUP 59<br />

2.4.2 Trace gas distributions from long-path DOAS measurements<br />

Participating scientist Andreas Hartl<br />

Abstract The possibility to retrieve 2D trace gas concentration fields from a limited number of longpath<br />

DOAS measurements was studied theoretically. Using a discrete approach it was found that the<br />

reconstruction can be tremendously improved by using optimal parametrisation of the unknown field,<br />

but its resolution is restricted by the number of light paths.<br />

100<br />

y<br />

0<br />

x<br />

100<br />

1<br />

conc.<br />

0.5<br />

0<br />

50<br />

x<br />

100<br />

50 y<br />

100<br />

conc.<br />

0.5<br />

Figure 2.26: (Left) Geometric arrangement with 3 telescopes and 36 light paths, (centre) 2D test<br />

distribution of 4 Gaussian concentration peaks and (right) its reconstruction by averaging over several<br />

bilinear discretisation grids.<br />

Background Experiments designed to give information<br />

on the spatial distribution of concentration<br />

fields are limited to certain scales and, if there<br />

are not enough measurements, they are sometimes<br />

hard to interpret. Point measurements are subject<br />

to all sorts of flucuations, path integrating<br />

absorption measuremts only provide average concentrations.<br />

While special processes, like plume<br />

development from a single point source or pollution<br />

in a street canyon, have been studied intensively,<br />

there is only little data available for others,<br />

e.g. distributions over a city region.<br />

This work examines 2D retrieval of concentration<br />

fields from ground-based DOAS measurements<br />

with artificial light sources on scales of a<br />

few km by techniques very similar to the ones used<br />

in conventional computerised tomography. These<br />

experimental concentration maps eventually can<br />

be used for the validation of chemical transport<br />

models, escpecially in cases where different model<br />

scales play a role.<br />

Funding BMBF through project 07 ATC-03<br />

(Young researchers fellowship program for research<br />

groups, AFO 2000-C).<br />

Methods and results The unknown concentration<br />

field is expressed in terms of a limited<br />

number of “basis” functions with local support<br />

and the discrete set of parameters is fit to the<br />

measurement data using a least squares principle.<br />

For the box and bilinear basis considered here, the<br />

1<br />

0<br />

50<br />

x<br />

100<br />

50 y<br />

100<br />

parameters represent values in the boxes and on<br />

the nodes of the discretisation grid, respectively.<br />

In the simulations, Gaussian peaks of varying half<br />

width serve as test distributions, motivated by the<br />

semi-empirical approach that describes turbulent<br />

transport and advection in the atmosphere by a<br />

diffusion model.<br />

We found that formulation of the problem, i.e.<br />

its parametrisation in terms of type and number<br />

of basis functions, plays a paramount role for the<br />

reconstruction quality. It turns out that the narrower<br />

the peaks, the finer the discretisation grid<br />

can be chosen, leading to systems with as many as<br />

four times unknowns than knowns - provided additional<br />

(physical or ad hoc) information is added.<br />

Bilinear function allow not only better discretisation,<br />

but also improved inversion of the problem<br />

and taking into account different discretisation<br />

grids can further reduce reconstruction errors.<br />

Reconstruction quality strongly depends on<br />

the light path geometry, Fig. 2.26 shows an example<br />

for one of the geometries exmamined.<br />

Outlook/Future work Application to high<br />

resolution model data for a heavily polluted<br />

area over Hannover, reconstruction from measurements<br />

in Heidelberg, further theoretical work on<br />

the estimation of the reconstruction error field,<br />

the inclusion of point measurements and the 3D<br />

case.<br />

Main Publication Hartl et al. [2005a]


60 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

2.4.3 Airborne measurements of the CH2O and NO2 distributions in the<br />

Po basin<br />

Participating scientists Klaus-Peter Heue, Ping Wang 2 and Irene Pundt<br />

2 <strong>Institut</strong> <strong>für</strong> Umweltphysisk, <strong>Universität</strong> Bremen<br />

Abstract During two FORMAT campaigns the Airborne Multi AXis DOAS (AMAXDOAS) instrument<br />

was used to determine the two dimensional formaldehyde and nitrogen dioxide distributions<br />

around Milano. Vertical distributions were retrieved from observed slant column densities from the<br />

spectra of six telescopes directed at different viewing angles.<br />

Figure 2.27: Formaldehyde average mixing ratio at 0-1000 m altitude along the flight track<br />

Background One of the major aims of the<br />

FORMAT project (FORMAldehyde as a tracer<br />

of photooxidation in the Troposphere) was to<br />

observe the different sources of photooxidating<br />

traces gases in the atmosphere. Fossil fuel combustion<br />

is known to be a source of NOx and<br />

VOCs. Other source of VOCs are biogenic emissions<br />

and natural fires. Formaldehyde is an important<br />

intermediate in the oxidation of VOCs.<br />

The AMAXDOAS observation results in differential<br />

slant column densities (dSCDs) for each of<br />

the ten telescopes. For the reference location the<br />

observed dSCD vanishes. In total 20 flights were<br />

performed during two campaigns in 2002 and 2003<br />

and the slant column of HCHO, NO2, O4 and<br />

SO2 were retrieved.<br />

Funding FORMAT, DOAS Tomography,<br />

SCIAMACHY validation<br />

Methods and results The observed signal of<br />

passive DOAS systems like the AMAXDOAS is<br />

strongly influenced by the aerosol content. Based<br />

on the O4 observations of all ten telescopes the<br />

aerosol content can be approximated for several<br />

measurement locations including the reference.<br />

The different telescopes have different sensibilities<br />

for O4 absorptions if the aerosol content<br />

changes. Using a radiative transfer model we<br />

modelled the O4 SCDs for several aerosol contents<br />

and compared them with the observations.<br />

The aerosol content affects the sensitivity of the<br />

different lines of sight. Based on the observations<br />

form five downward directed lines of sight<br />

the CH2O vertical columns along the flight can<br />

be deduced. However, the measurement principle<br />

requires some approximations about the CH2O<br />

concentration at the reference location. Assuming<br />

a standard profile, based on independent measurements,<br />

an average mixing ratio for the lowest 1000<br />

m can be retrieved. Figure 2.27 shows the average<br />

CH2O mixing ratio distribution around Milano<br />

on 16/08/2002. On this day the wind blew<br />

from south east, therefore in the north west of the<br />

town an enhanced HCHO concentration is observed.<br />

The emission plume of Milano was found<br />

to be 20 km wide and the net CH2O production<br />

is estimated at 0.6 tons/hour.<br />

Outlook/Future work Publication is in<br />

preparation.<br />

Main publications Heue [2005]


2.4. DOAS TOMOGRAPHY GROUP 61<br />

2.4.4 Development of a Multibeam instrument for simultaneous measurements<br />

along multiple light paths<br />

Participating scientists Kai Uwe Mettendorf and Irene Pundt<br />

Abstract Long path DOAS tomography uses multiple Long path DOAS instruments and intersecting<br />

light paths to retrieve the concentration distributions of certain trace gases. For these measurements<br />

a new DOAS instrument was developed. Three instruments were build.<br />

Figure 2.28: Instrumental setup of the entire Multibeam system (including, A, telescope; B, lamp<br />

housing; C, mode mixer; D, spectrograph; E, CCD detector; F, stepper motor controller; G, mirror<br />

tower with four mirror units; H, rotating disk retroreflector; I, retroreflector array at a distance<br />

between 500 and 5000 m). The distance between the telescope and the mirror tower is usually 10-15<br />

m. The distance between the rotating retroreflector and the tower is also 10-15 m. The rotating disk<br />

can be placed close to the telescope.<br />

Background Conventional Long-path DOAS<br />

Instruments emit a single light beam. For two<br />

dimensional DOAS-tomographic-measurements,<br />

however at least 10-40 light paths are necessary.<br />

The Multibeam DOAS instrument, which emits<br />

one to six light paths was developed for this purpose.<br />

Funding DOAS Tomography (BMBF)<br />

Methods and results A novel long-path differential<br />

optical absorption spectroscopy (DOAS)<br />

apparatus for measuring tropospheric trace gases<br />

the ”Multibeam” instrument was developed. It is<br />

the first active DOAS device that emits several<br />

light beams simultaneously through only one telescope<br />

and with only one lamp as a light source,<br />

allowing simultaneous measurement along multiple<br />

light paths. In contrast to conventional<br />

DOAS instruments, several small mirrors are positioned<br />

near the lamp, creating multiple virtual<br />

light sources that emit one light beam each in one<br />

specific direction. The possibility of error due to<br />

scattering between the light beams is negligible.<br />

The trace-gas detection limits of NO2, SO2, O3,<br />

and H2CO are similar to those of the traditional<br />

long-path DOAS instrument. However, the received<br />

light intensity is reduced by a factor of 3<br />

compared to a traditional long-path DOAS instrument<br />

with a similar main mirror.<br />

Main publication Pundt & Mettendorf [2005],<br />

Mettendorf [2005]


62 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

2.4.5 An Indoor Test Campaign of the Tomography Long Path Differential<br />

Optical Absorption Spectroscopy (DOAS) Technique<br />

Participating scientists Kai Uwe Mettendorf, Andreas Hartl and Irene Pundt<br />

Abstract For the validation of the LP-DOAS-tomography method and the test of the Multibeam<br />

DOAS instrument an indoor validation campaign was performed. Known concentration distributions<br />

were successfully measured by 39 intersecting light paths and reconstructed using the SIRT-method.<br />

Figure 2.29: Reconstruction of a concentration distribution by SIRT on a 12×12 pixel grid and with<br />

additional grid shifting. The upper panel shows the original concentration distribution, the lower left<br />

panel the result from modelled column densities and the lower right panel the result from measured<br />

column densities.<br />

Background Long path DOAS tomography is<br />

a novel application of the DOAS-method which<br />

was not been validated before.<br />

Funding DOAS Tomography (BMBF)<br />

Methods and results In this study the twodimensional<br />

long path DOAS tomography measurement<br />

technique was validated by an indoor experiment<br />

with well-known concentration distributions.<br />

The experiment was conducted over an area<br />

of 10m×15m using one and two cylindrical containers<br />

of diameter 2 m, respectively, filled with<br />

NO2. The setup was realized with three of the recently<br />

developed Multibeam instruments (Pundt<br />

and Mettendorf, 2005), which allow the simultaneous<br />

measurement along at least four light paths<br />

each. The configuration consisted of twelve simultaneous<br />

light beams, 39 horizontal light paths in<br />

total, and 16 different cylinder positions inside the<br />

field. It was found that for the discretization and<br />

inversion technique shown here reconstructions of<br />

the concentration distributions from experimental<br />

data agree well with simulated reconstructions. In<br />

order to draw conclusions for atmospheric applications,<br />

numerical studies including instrumental errors<br />

were carried out. It was concluded that with<br />

the presented measurement setup it should be possible<br />

to measure and reconstruct one or two NO2<br />

plumes of 600 m diameter and average concentrations<br />

above 4.2 ppbv each, to a scale of 13.5 km 2 .<br />

Theoretical investigations show that it should be<br />

possible to localize and quantify 600 m diameter<br />

plumes of SO2 > 1.5 ppbv, H2CO > 6.3 ppbv,<br />

HONO > 3.2 ppbv, and O3 > 46.2 ppbv.<br />

Main publication Mettendorf [2005]


2.4. DOAS TOMOGRAPHY GROUP 63<br />

2.4.6 2D and 3D tomographic LP-DOAS measurements of trace gas distributions<br />

in Heidelberg over an area of 4 ∗ 4 km 2<br />

Participating scientists Denis Poehler, Alexander Stelzer, Irene Pundt<br />

Abstract A configuration of three Multibeam LP-DOAS Instruments and 20 different light paths<br />

to retro reflector arrays was established for long term 2D and 3D measurements of NO2, SO2, O3,<br />

HCHO, and HONO over an area of a 4 ∗ 4 km 2 above the city centre of Heidelberg.<br />

Figure 2.30: 3 Dimensional view on all light paths of the measurement over an area of 4 ∗ 4 km 2 with<br />

three telescope locations: IUP, SAS and HD-Druck.<br />

Background LP-DOAS (Long Path Differential<br />

Absorption Spectroscopy) is a well known<br />

technique for measuring average concentrations of<br />

tropospheric trace gases along a light path extending<br />

between a telescope and a retro reflector. But<br />

single path measurements are often not sufficient<br />

(as well as single point measurements), if smallscale<br />

variations exist or transport is important.<br />

To obtain informations of the dispersion, it is necessary<br />

to measure along a couple of light paths.<br />

The development of the ”Multibeam LP-DOAS<br />

telescope” (Pundt and Mettendorf, 2005), allows<br />

the measurement along up to 6 light paths simultaneously.<br />

With the suitable combination of<br />

two or more Multibeam LP-DOAS telescopes and<br />

the use of tomographic reconstruction techniques<br />

good quality 2D and 3D reconstructions of the<br />

measured trace gases can be achieved.<br />

Funding German Ministry of Research and Education<br />

, AFO 2000-C, project 07 ATC-03<br />

Methods and results The experimental setup<br />

consists of 3 Multibeam telescopes located on top<br />

of high buildings in the city (IUP, HD-Druck and<br />

SAS) and 20 retro reflector arrays. This work focuses<br />

on the one hand on the telescope location<br />

HD-Druck, where a Multibeam Instrument was<br />

installed and modified, to allow automatic measurements<br />

from this place.<br />

Each of the three telescopes uses a Xe-Arc lamp as<br />

light source, which creates up to 6 parallel light<br />

beams using different mirrors. Each light beam<br />

can be redirected to different retro reflector arrays<br />

which reflect parts of the light back into the<br />

telescope. The received light is measured with a<br />

Czerny Turner Spectrograph and contains information’s<br />

of the trace gas absorptions. With the<br />

measurement between 285 nm and 365 nm and<br />

the use of the DOAS technique reconstruction of<br />

NO2, SO2, O3, HCHO, and HONO are made<br />

along each light path.<br />

During the first measurements it was mostly impossible<br />

to run all three telescopes simultaneously,<br />

due to many breakdowns of the sensitive experimental<br />

setup. But since simultaneous measurements<br />

of all light paths are necessary for tomographic<br />

inversions, the hardware was modified and<br />

new controller software was coded to improve the<br />

stability. First simultaneous measurements were<br />

performed in September 2005, but are not completely<br />

analysed yet.<br />

Outlook/Future work The system will be run<br />

continuously over a time scale of several months.<br />

For the periods of simultaneous measurement<br />

data, 2 dimensional trace gas distributions will<br />

be reconstructed.<br />

Main publication Poehler et al. [2005]


64 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

2.4.7 Two-dimensional measurement of motorway emission plumes<br />

Participating scientist Irene Pundt, Kai Uwe Mettendorf<br />

Abstract A first Long-path Tom-DOAS experiment was carried out in April/May 2001 next to<br />

the German motorway A656 (between Heidelberg and Mannheim), as part of the BAB II campaign<br />

(Fiedler et al., 2001). From the measurements along 16 different light paths vertical profiles on both<br />

sides of the motorway as well as two-dimensional maps of the NO2, SO2 and ozone concentration<br />

distributions could be derived. Emission factors were calculated and compared to model simulations.<br />

Figure 2.31: Left: Tomographic setup used during a motorway emission campaign. From each telescope<br />

one light beam is directed successively towards the eight retro reflectors (circles). Right: NO2<br />

motor vehicle emission plume perpendicular to a motorway (in ppbv). Black bar: Location of the<br />

motorway, chequered area: Experiment towers, wind direction: coming from the left.<br />

Background Traffic emissions are among the<br />

major sources for anthropogenic air pollution.<br />

Volatile compounds and nitrogen oxides (NOx)<br />

are, besides others, important components of<br />

these emissions. Vehicle emission factors are generally<br />

estimated by means of dynamometric test<br />

measurements, but they may change under real<br />

world conditions. Therefore, a couple of field studies,<br />

mostly performed inside tunnels, have been<br />

conducted. However, the air flow through tunnels<br />

is influenced by the moving cars, causing an artificial<br />

wind, which changes the traffic emissions. A<br />

more realistic approach to evaluate emission factors<br />

is to carry out measurements at an open road.<br />

Knowledge of vertical profiles on both sides of the<br />

road is necessary to calculate emission rates (in<br />

molecules s −1 m −1 ). Taking 2D images of the<br />

emission plume perpendicular to the line source<br />

can provide even more information than emission<br />

rates. 2D images can be used to validate 2D<br />

dispersion models, or in the case of short lived<br />

species, to validate 2D chemical transport models.<br />

Funding TOMDOAS (BMBF)<br />

Methods and results The tomographic arrangement<br />

consisted of two long path telescope<br />

sites (one at each side of the motorway), and eight<br />

retro reflector arrays (four on each side at different<br />

heights). Each of the telescopes emitted<br />

one light beam, which was successively directed to<br />

the different retro-reflectors. Altogether 16 different<br />

light paths were realised. 2D NO2 concentration<br />

distributions perpendicular to the motorway<br />

were derived for several time spans (right figure).<br />

Concentrations on the left-hand side of the figure<br />

represent the NO2 background abundance and<br />

the right-hand side the background concentration<br />

plus emissions. For the inversion, an algebraic reconstruction<br />

technique was used in combination<br />

with bilinear basis functions describing the distribution.<br />

The derived emission plumes are, within<br />

the errors, in good agreement with model expectations.<br />

To our knowledge, these are the first measurements<br />

of two dimensional sections of an emission<br />

plume from a line source. Using multibeam<br />

telescopes will increase the time resolution of the<br />

images from hours to minute ranges in the future.<br />

Outlook/Future work SO2 and HCHO emission<br />

rates are currently evaluated and compared<br />

to model simulations. Ozone distributions seem to<br />

be not consistent with model expectations. Further<br />

work is needed to understand the discrepancies.<br />

Main publication Pundt et al. [2005c], Laepple<br />

et al. [2004], Mettendorf [2005]


2.4. DOAS TOMOGRAPHY GROUP 65<br />

2.4.8 Two dimensional concentration distributions of a NO2 Emission plume<br />

from a point source derived by Airborne DOAS Tomography<br />

Participating scientists Irene Pundt, Klaus-Peter Heue, Bing-Chao Song<br />

Abstract First airborne DOAS tomography measurements of two-dimensional concentration crosssections<br />

of a plume from a point source have been carried out. The measurements were performed<br />

with an AMAXDOAS (Airborne Multi-AXis Differential Optical Absorption Spectroscopy) instrument<br />

onboard a small aircraft during the second campaign of the European FORMAT project in August /<br />

September 2003.<br />

Figure 2.32: Left: Lines of sight of the flight track as function of the geographic position of the Sermide<br />

power plant plume. X is the latitudinal, y the longitudinal and z the vertical direction. For clearness,<br />

only the downward looking viewing directions are shown neglecting the scattering of light. The colors<br />

of the lines indicate the NO2 slant column densities along each of them. Right: NO2 2D mixing ratio<br />

distributions of the Sermide plume after tomographic inversion, first pass (distance from the plant: 5<br />

km).<br />

Background The focus of this study is the first<br />

application of the Airborne DOAS Tomography<br />

technique to provide concentration distributions<br />

of NO2 along cross sections of a plume from a<br />

point source. A technique to formulate a two dimensional<br />

inversion problem with weighting matrices<br />

from single scattering radiative transfer simulations,<br />

which can be used for tomographic inversions,<br />

is presented.<br />

Funding TomDOAS (BMBF), FORMAT (EU)<br />

Methods and results As part of the second<br />

campaign of the European FORMAT project<br />

(FORMAldehyde as a tracer of photo oxidation<br />

in the Troposphere), the instrument was installed<br />

on board a Partenavia PA 68 aircraft. During one<br />

occasion, on 26 September 2003, it was possible to<br />

derive the information for two-dimensional reconstructions<br />

of an emission plume of a point source.<br />

Three over flights were performed across the emission<br />

plume of the NO2 emitting Sermide power<br />

plant, located at 45.02 degree N 11.25 degree E.<br />

Three reconstructions have been performed, one<br />

for each overpass. It is assumed that the plume<br />

has not changed during the course of the measurement.<br />

Therefore 5, 6 and 9 aircraft positions, re-<br />

sulting in 50, 60 and 90 lines of sight were included<br />

for the 1st, 2nd and 3rd overpass, respectively (left<br />

figure). For each overpass, the area of interest<br />

is divided into rectangular boxes with 16 vertical<br />

segments of 133 m height and horizontal segments<br />

of 1.5 km length. For each inversion, the weighting<br />

matrix was calculated for the respective 2D<br />

grid. Then the inversion is performed using the<br />

Simultaneous Iterative Reconstruction Technique<br />

(SIRT) method. The right Figure presents the resulting<br />

NO2 mixing ratio maps for the first overpass.<br />

Interestingly the first and the third overpass,<br />

which were conducted very close by, show<br />

similar shapes, indicating only small changes of<br />

the plume during the 12 minutes flight interval.<br />

From this finding we conclude that the quality of<br />

the reconstruction is reproducible and consistent.<br />

NOX emissions of 4.1-9.6 10 24 molec s −1 were<br />

derived, in agreement with the information given<br />

by the power plant company.<br />

Outlook/Future work The analysis of the<br />

FORMAT flights is ongoing.<br />

Main publication Pundt et al. [2005a], Heue<br />

[2005]


66 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

2.4.9 Development of a computer tool for the inversion and optimization<br />

of airborne tomographic DOAS measurements (Tomolab2)<br />

Participating scientist Bing-Chao Song, Andreas Hartl and Irene Pundt<br />

Abstract The tomographic DOAS software project Tomolab [Laepple et al., 2004] is further developed<br />

for Airborne Multi Axis DOAS (AMAXDOAS) measurements. With its ability to include<br />

scattered light paths it can be used to optimize airborne measurements, optimize measurement geometries<br />

and for the reconstruction of 2D/3D concentration fields.<br />

Figure 2.33: Flight track with ground-reflected light paths (left), 2D single scattering light path<br />

geometry and reconstruction (right) in Tomolab2.<br />

Background The Tomolab software was originally<br />

created especially for ground-based active<br />

measurements, i.e. light paths clearly defined by<br />

source and reflector. While it is efficient for analyzing<br />

and displaying simple geometries, it does<br />

not include scattering processes, neither in its<br />

graphics nor in its inversion part. Tomolab was<br />

designed as a Windows project and runs on personal<br />

computers only. The enhanced version Tomolab2<br />

removes the dependency of the Windows<br />

system and, for intensive calculations, can be run<br />

on any UNIX workstation. Very flexible scripting<br />

support simplifies case studies for different geometric<br />

settings and atmospheric conditions.<br />

Funding DOAS Tomography, BMBF<br />

Method Single scattering processes, usually<br />

dominating the atmospheric radiative transfer,<br />

are simulated by defining a group of partial light<br />

paths which all enter the telescope and add up to<br />

the same measurement signal. Their individual<br />

contributions to the total absorption captured by<br />

the telescope are weighted by their relative light<br />

intensities from radiative transfer calculation for<br />

the layer where the scattering event took place.<br />

We finally obtain box air mass factors (AMFs)<br />

for cases where single scattering dominates. Measurements<br />

where multiple scattering is not negligi-<br />

ble can also be simulated and reconstructed, but<br />

the corresponding 2D or 3D box AMFs have to<br />

be calculated by suitable radiative transfer models.<br />

The modular structure of Tomolab2 makes<br />

exchange of platform dependent code easier. The<br />

visualization part is currently implemented for the<br />

Windows system. The scripting support layer for<br />

Windows is implemented using the so called COM<br />

technique. Essential and common functions are<br />

encapsulated into binary components to ensure<br />

the stability of the project. Varying case studies<br />

can be done by scripting components without<br />

modifying Tomolab2’s code.<br />

Results The Tomolab2 project was developed<br />

for passive airborne DOAS measurements and<br />

designed aiming at a flexible and platformindependent<br />

structure. 2D box AMFs have been<br />

calculated for lightly polluted scenarios and compare<br />

well with those from a radiative transfer<br />

model. The program also has been tested on<br />

UNIX platforms. Thanks to its modular structure,<br />

Tomolab2 can easily be updated and maintained.<br />

Outlook/Future work 3D reconstruction.<br />

Embedding of radiative transfer models for operational<br />

usage.


2.4. DOAS TOMOGRAPHY GROUP 67<br />

References<br />

Bäuerle, A. 2004. Messung von Spurenstoffverteilungen in Mailand mit Hilfe eines Multistrahl-<br />

Langpfad Teleskops. Staatsexamensarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />

Bruns, M., Buehler, S. A., Burrows, J. P., Heue, K.-P., Platt, U., Pundt, I., Richter, A., Rozanov, A.,<br />

Wagner, T., & Wang, P. 2004. Retrieval of profile information from Airborne Multi Axis UV/visible<br />

skylight absorption measurements. Appl.Opt., 43(22), 4415 – 4426.<br />

Bruns, M., Buehler, S. A., Burrows, J. P., Richter, A., Rozanov, A., Wang, P., Heue, K.-P., Platt, U.,<br />

Pundt, I., & Wagner, T. 2005. NO2 Profile retrieval using airborne multi axis UV-visible skylight<br />

absorption measurements over central Europe. Atmos. Chem. Phys. Discuss. accepted.<br />

Fix, A., Ehret, G., Flentje, H., Poberaj, G., Gottwald, M., Finkenzeller, H., Bremer, H., Bruns, M.,<br />

Burrows, J. P., Kleinbhl, A., Kllmann, H., Kuttippurath, J., Richter, A., Wang, P., Heue, K.-<br />

P., Platt, U., Pundt, I., & Wagner, T. 2005. SCIAMACHY validation by aircraft remote sensing:<br />

design, execution, and first measurement results of the SCIA-VALUE mission. Atmos. Chem. Phys.,<br />

5, 1273 – 1289.<br />

Hak, C., Pundt, I., Trick, S., Kern, C., Platt, U., Dommen, J., Ordóˆnez, C., Prévôt, A. S. H.,<br />

Junkermann, W., Astorga-Lloréns, C., Larsen, B. R., Mellqvist, J., Strandberg, A., Yu, Y., Galle,<br />

B., Kleffmann, J., Lörzer, J., Braathen, G. O., & Volkamer, R. 2005. Intercomparison of four<br />

different in-situ techniques for ambient formaldehyde measurements in urban air. Atmos. Chem.<br />

Phys., 5, 2881 – 2900.<br />

Hartl, A., Song, B.-C., & Pundt, I. 2005a. Reconstructing 2d-Concentration Peaks from Long Path<br />

DOAS-Tomographic measurements: Parametrisation and Geometry within a Discrete Approach.<br />

Atmos. Chem. Phys. Discuss., 5, 11781 – 11819.<br />

Hartl, A., Mettenorf, K. U., Song, B. C., & Pundt, I. 2005b. Reconstruction of 2D-Trace Gas<br />

Concentration Distributions from Long-path DOAS Measurements: General Approach, Validation<br />

and Simulations for an Experiment on an Urban Site. In: Proceedings of the 31st ”International<br />

Symposium of Remote Sensing of the Environment”, June 20-24, 2005, in St. Petersburg, Russia.<br />

ISPRS-publication(CD-ROM).<br />

Heckel, A., Richter, A., Tarsu, T., Wittrock, F., Hak, C., Pundt, I., Junkermann, W., & Burrows,<br />

J. P. 2005. MAX-DOAS measurements of formaldehyde in the Po-Valley. Atmos. Chem. Phys., 5,<br />

909 – 918.<br />

Heue, K.-P. 2005. Airborne Multi Axis DOAS instrument and measurements of two dimensional<br />

tropospheric trace gas distributions. Ph.D. thesis, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg,<br />

Germany.<br />

Heue, K.-P., Beirle, S., Bruns, M., Burrows, J. P., Platt, U., Pundt, I., Richter, A., Wagner, T., &<br />

P. Wang, P. 2004. SCIAMACHY validation using the AMAXDOAS instrument. In: Proceedings<br />

of the ENVISAT & ERS Symposium, 6-10 September 2004, Salzburg, Austria. ESA-publication<br />

SP-572 (CD-ROM).<br />

Heue, K.-P., Richter, A., Bruns, M., Burrows, J. P., Friedeburg, C. von, Platt, U., Pundt, I., Wang,<br />

P., & Wagner, T. 2005. Validation of SCIAMACHY tropospheric NO2-columns with AMAXDOAS<br />

measurements. Atmos. Chem. Phys., 5, 1039 – 1051.<br />

I., I. Pundt, Mettendorf, K.U., & v. Friedeburg, C. 2005. Emissionsmessung von NO2, SO2 und O2<br />

mittels DOAS Fernerkundung. Invited talk at the workshop ”Validierung von Kfz-Emissionsdaten:<br />

Das <strong>Karls</strong>ruher Autobahnprojekt BAB II”, <strong>Karls</strong>ruhe, 01.12.2005.<br />

Knab, V. 2004. Basic theory on DOAS tomography, Reconstruction of 2D trace gas distributions by<br />

discrete linear inversion techniques. Diplomarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg,<br />

Germany.<br />

Kunz, C. 2001. Charakterisierung eines Multi-Strahl-Langpfad-DOAS-Systems zur Messung von<br />

Spurenstoff-Konzentrationen in der Atmosphre. Staatsexamensarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>,<br />

<strong>Universität</strong> Heidelberg, Germany.


68 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

Laepple, T., Knab, V., Mettendorf, K.-U., & Pundt, I. 2004. Longpath DOAS tomography on a<br />

motorway exhaust plume: Numerical studies and application to data from the BAB II campaign.<br />

Atmos. Chem. Phys., 4, 1323 – 1342.<br />

Lösch, J. 2001. Bestimmung von NO2 und SO2 Emissionen von Kraftfahrzeugen mittels DOAS-<br />

Tomographie. Diplomarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />

Mettendorf, K. U. 2005. Aufbau und Einsatz eines Multibeam Instrumentes zur DOAStomographischen<br />

Messung zweidimensionaler Konzentrationsverteilungen. Ph.D. thesis, <strong>Institut</strong><br />

<strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />

Mettendorf, K. U., Hartl, A., & Pundt, I. 2005. An indoor test campaign of the Tomography Long<br />

Path Differential Absorption Spectroscopy (DOAS). J. Environ. Monit. accepted.<br />

Poehler, D., Rippel, B., Stelzer, A., Mettendorf, K. U., Hartl, A., Platt, U., & Pundt, I. 2005.<br />

Instrumental setup and measurement configuration for 2D-tomographic DOAS measurements of<br />

trace gas distributions over an area of a few square km. In: Proceedings of the 31st ”International<br />

Symposium of Remote Sensing of the Environment”, June 20-24, 2005, in St. Petersburg, Russia.<br />

ISPRS-publication(CD-ROM).<br />

Pundt, I. 2005a. DOAS (Differentielle Optische Absorptions- Spektroskopie)Messungen mit neuester<br />

Technologie. Invited talk at the DECHEMA/GDCH/DGB-Gemeinschaftsausschuss Chemie der<br />

Atmosphre, Frankfurt, 22.04.2005.<br />

Pundt, I. 2005b. DOAS tomography for the localisation and quantification of anthropogenic air<br />

pollution. Anal. Bioanal. Chem. accepted.<br />

Pundt, I., & Mettendorf, K. U. 2005. Multibeam long-path differential optical absorption spectroscopy<br />

instrument: a device for simultaneous measurements along multiple light paths. Appl. Opt., 44(23),<br />

4985 – 4994.<br />

Pundt, I., Heue, K.-P., Song, B.-C., Wagner, T., Bruns, M., Burrows, J. P., Richter, A., & Wang, P.<br />

2005a. Airborne tomographic measurements of NO2 Plumes from point sources using the AMAX-<br />

DOAS instrument. J. Geophys. Res. submitted.<br />

Pundt, I., Hak, C., Hartl, A., Heue, K.-P., Mettendorf, K. U., Platt, U., Poehler, D., Rippel, B.,<br />

Song, B.-C., Stelzer, A., Wagner, T., Bruns, M., Burrows, J. P., Richter, A., & Wang, P. 2005b.<br />

Mapping of tropospheric trace gas concentration distributions from ground and aircraft by DOAStomography<br />

(Tom-DOAS). In: Proceedings of the 31st ”International Symposium of Remote Sensing<br />

of the Environment”, June 20-24, 2005, in St. Petersburg, Russia. ISPRS-publication(CD-ROM).<br />

Pundt, I., Mettendorf, K. U., Laepple, T., Knab, V., Xie, P., Lösch, J., Friedeburg, C. von, Platt, U.,<br />

& Wagner, T. 2005c. Measurements of trace gas distributions using Long-path DOAS-Tomography<br />

during the motorway campaign BAB II: experimental setup and results for NO2. J. Atmos. Environ.,<br />

39(5), 967 – 975.<br />

Rippel, B. 2005. Vorarbeiten <strong>für</strong> Langpfad DOAS Tomographische Messungen über der Stadt Heidelberg.<br />

Diplomarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />

Stelzer, A. 2005. Horizontale tomographische Langpfad-DOAS Spurengasmessungen in Heidelberg.<br />

Diplomarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />

von Friedeburg, C., Pundt, I., Mettendorf, K. U., Wagner, T., & Platt, U. 2005. Multi-axis-DOAS<br />

measurements of NO2 during the BAB II motorway emission campaign. J. Atmos. Environ., 39(5),<br />

977 – 985.<br />

Wang, P., Richter, A., Bruns, M., Burrows, J. P., Junkermann, W., Heue, K.-P., Wagner, T., Platt,<br />

U., & Pundt, I. 2005a. Airborne multi-axis DOAS measurements of tropospheric SO2 plumes in<br />

the Po-valley, Italy. Atmos. Chem. Phys. Discuss, 5, 2017 – 2045.<br />

Wang, P., Richter, A., Bruns, M., Rozanov, V., Burrows, J. P., Heue, K.-P., Wagner, T., Pundt, I., &<br />

Platt, U. 2005b. Measurements of tropospheric NO2 with an airborne multi-axis DOAS instrument.<br />

Atmos. Chem. Phys., 5, 337 – 343.


2.5. SATELLITE GROUP 69<br />

2.5 Satellite Group<br />

Participating scientist Steffen Beirle, Tim Deutschmann, Barbara Dix, Ossama Ibrahim, Christian<br />

Frankenberg, Michael Grzegorski, Klaus-Peter Heue, Jens Hollwedel, Muhammad Fahim Khokhar,<br />

Sven Kühl, Thiery Marbach, Janis Pukite, Suniti Sanghavi, Thomas Wagner, and Walburga Wilms-<br />

Grabe<br />

Abstract The Satellitegroup is part of the researchgroup Atmospheric Physics of Prof. Dr. Ulrich<br />

Platt. The satellite born remote sensing of the Earth’s atmosphere at the University of Heidelberg<br />

started in 1996 with the retrieval of atmospheric trace gases, namely NO2 and BrO. Today a wide variety<br />

of trace gases and other atmospheric parameters (Aerosols, Clouds, Radiative Transfer) from different<br />

satellite instruments are investigated at the IUP (see also http://satellite.iup.uni-heidelberg.de).<br />

Figure 2.34: Satellite measurement of the reflected and scattered sun light (yellow). The spectral<br />

signatures of several atmospheric trace gases are analysed in selected spectral ranges using the DOAS<br />

method. Displayed are the fitting results for various species analysed in the satellite group.<br />

Overarching topic and Background For about 10 years now, a new generation of UV/vis/NIR<br />

satellite instruments (GOME, SCIAMACHY, OMI) with moderate spectral resolution allows the<br />

retrieval of a large variety of atmospheric trace gases. In particular, global maps of several tropospheric<br />

trace gases like O3, BrO, NO2, CO, CH4, CO2, HCHO, SO2, H2O, O2, O4, and cloud properties can<br />

be analysed from observations in nadir viewing mode. The most important advantage of such satellite<br />

observations is their spatial (horizontal) coverage and resolution. The latest generation of nadir looking<br />

UV/vis satellite instruments (e.g. OMI) achieves global coverage within one day and has a horizontal<br />

resolution of about 13 x 24 km 2 . From such satellite observations, various individual sources like large<br />

cities can be identified. In addition, the observation of scattered sun light in limb geometry allows to<br />

retrieve vertical profiles of several stratospheric trace gases like O3, NO2, BrO and OClO.<br />

Funding The group activities are funded through various national and international projects, e.g.<br />

SCIAMACHY validation, FORMAT, STAR, Tropische Tropopause, NOXTRAM, EVERGREEN, AC-<br />

CENT<br />

Main methods From the measured spectra, the narowband absorption features of several trace<br />

gases are analysed using the DOAS method (see Figure). The result of the spectral analysis represents<br />

the trace gas absorption integrated along the absorption path. In addition, also the broad band<br />

spectral features are analysed; they yield information in particular on the cloud cover, aerosol load and<br />

ground albedo. Various algorithms for the analysis of satellite spectra were developed in the satellite<br />

group within the last years. For the detailed interpretation of the analysed spectral information,<br />

radiative transfer modelling is needed. A 3-D Monte-Carlo radiative transfer model (TRACY) was<br />

developed in our group, which allows to simulate various complex viewing geometries and atmospheric<br />

properties. The retrieved global data sets are further investigated using image sequence techniques.


70 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

Subprojects The various projects can be classified according to their spectral range, viewing geometry,<br />

and analysis method.<br />

UV/vis DOAS for Nadir viewing geometry: The main target is the determination of global maps of<br />

tropospheric trace gas distributions like NO2, BrO, H2O, HCHO, SO2. Curently measurements of<br />

GOME and SCIAMACHY are under investigation.<br />

NIR DOAS for Nadir viewing geometry: The main target is the determination of global maps of<br />

tropospheric trace gas distributions like CH4, CO2, and CO. Measurements in the near IR spectral<br />

range are caried out only by SCIAMACHY.<br />

Cloud retrieval for Nadir viewing geometry: The main target is the determination of global maps of<br />

cloud cover (effective cloud fraction) from broad band spectral measurements. From the combination<br />

with narow band absorption measurements of O4 and O2, also additional parameters like cloud top<br />

height can be retrieved.<br />

UV/vis DOAS for limb viewing geometry: The main target is the determination of vertical profiles of<br />

stratospheric trace gases like O3, NO2, BrO, and OClO. Measurements in limb viewing geometry are<br />

caried out only by SCIAMACHY.<br />

3-D radiative transfer modelling: Detailed radiative transfer modelling is the prerequisite for the corect<br />

interpretation of the results of the spectral analysis. The full spherical 3-dimensional Monte Carlo<br />

model is developed and operated in our group. Also a detailed scheme for the simulation of radiative<br />

properties of aerosols is developed.<br />

Validation of satellite data with independent DOAS observations are caried out from several ground<br />

based stations (Kiruna, Paramaribo, Neumayer) as well as from aircrafts and ships.<br />

Intensive interaction and cooperation exists with various international groups, e.g. Uni Bremen, IASB<br />

Brussels, Uni München, SRON Utrecht, KNMI Utrecht, EUMETSAT<br />

Publications<br />

Peer Reviewed Publications<br />

1. Frankenberg et al. [2005a]<br />

2. Frankenberg et al. [2005c]<br />

3. Frankenberg et al. [2005b]<br />

4. Heue et al. [2005]<br />

5. Hollwedel et al. [2004]<br />

6. Khokhar et al. [2005]<br />

7. Kühl et al. [2004]<br />

8. Richter et al. [2005]<br />

9. Wagner et al. [2005a]<br />

10. Wagner et al. [2004]<br />

11. Wagner et al. [2005b]<br />

Grey Publications<br />

1. Grzegorski et al. [2004]<br />

2. Heue et al. [2004]<br />

3. Marbach et al. [2004]<br />

4. ACCENT [2005]<br />

5. Wilms-Grabe et al. [2004]


2.5. SATELLITE GROUP 71<br />

PhD Theses<br />

1. Beirle [2004]<br />

2. Frankenberg [2005]<br />

3. Heue [2005]<br />

4. Hollwedel [2005]<br />

5. Kühl [2005]<br />

Diploma Theses<br />

1. Halasia [2004]<br />

Invited Talks<br />

1. Wagner [2004a]<br />

2. Wagner [2004b]<br />

3. Wagner [2004c]<br />

4. Wagner [2004d]<br />

5. Wagner [2005a]<br />

6. Wagner [2005c]<br />

7. Wagner [2005b]


72 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

2.5.1 Quantifying NOx from lightning using satellite data<br />

Participating scientists Steffen Beirle, Thomas Wagner, Ulrich Platt<br />

Abstract A strong lightning event in the Gulf of Mexico was investigated. Using satellite based<br />

measurements of NO2, combined with ground based flash counts, the direct observation of freshly<br />

produced lightning NOx could be demonstrated, and the amount of the produced NOx has been<br />

estimated.<br />

Figure 2.35: Lightning event on 30 August in the Gulf of Mexico. (a) NO2 TVCD from GOME (10 15<br />

molec/cm 2 ). (b) Time of flashes detected by NLDN<br />

Background Nitrogen oxides (NOx=<br />

NO+NO2) play an important role in tropospheric<br />

chemistry, in particular in catalytic ozone production.<br />

Lightning provides a natural source of<br />

nitrogen oxides, dominating the production in the<br />

tropical upper troposphere, with strong impact<br />

on tropospheric ozone and the atmosphere’s oxidizing<br />

capacity. Recent estimates of lightning<br />

produced NOx (LNOx) are of the order of 5 Tg<br />

[N] per year with still high uncertainties in the<br />

range of one order of magnitude. The Global<br />

Ozone Monitoring Experiment (GOME) on board<br />

the ESA–satellite ERS–2 allows the retrieval of<br />

tropospheric vertical column densities (TVCDs)<br />

of NO2 on a global scale. Here we present the<br />

GOME NO2 measurement directly over a large<br />

convective system over the Gulf of Mexico.<br />

Funding See satellite group overview.<br />

Methods and results A unique event of<br />

GOME capturing LNOx just produced is found<br />

on 30 August 2000 over the Gulf of Mexico: A<br />

sequence of about 14 pixels, measured at 16:47-<br />

16:48 UTC, shows high tropospheric NO2 TCDs<br />

(Fig. 1a) that by far exceed normal levels over<br />

ocean.<br />

These high TVCDs coincide with a strong convective<br />

system causing high lightning activity.<br />

Fig. 1b depicts the flashes detected by the U.S.<br />

National Lightning Detection Network (NLDN)<br />

on 30 August 2000 before the ERS–2 overpass,<br />

while the time of the flash occurence is colorcoded.<br />

This particular event is unprecedented as the<br />

lightning activity coincides perfectly with the<br />

GOME measurement both in space and in time.<br />

The enhanced NO2 TVCDs can not be explained<br />

with transport of anthropogenic emissions and<br />

must be thus due to freshly produced LNOx. As<br />

far as we know, such a clear and direct detection<br />

of LNOx from satellite has never been reported<br />

before.<br />

A quantitative analysis yields a LNOx production<br />

of 77 (27-230) moles of NOx, or 1.1 (0.4-3.2) kg<br />

[N], per flash. If simply extrapolated, this coresponds<br />

to a global LNOx production of 1.5 (0.5-<br />

4.5) Tg [N]/yr.<br />

Outlook/Future work The analysis of lightning<br />

NOx from satellite data will be continued<br />

with particular focus on radiative transfer in thunderstorm<br />

clouds.<br />

Main publication Beirle et al. [2005]


2.5. SATELLITE GROUP 73<br />

2.5.2 Evaluation of global tropospheric NO2 from SCIAMACHY<br />

Participating scientists Steffen Beirle, Thomas Wagner, Ulrich Platt<br />

Abstract Spectral measurements from the satellite instrument SCIAMACHY allow to determine<br />

tropospheric column densities of NO2 with improved spatial resolution compared to its predecessor<br />

GOME. The time series of global measurements provide valuable information on the spatial distribution<br />

of NOx pollution, allowing to identify and quantify the different sources of NOx.<br />

Figure 2.36: Mean NO2 TVCD (10 15 molec/cm 2 ) from SCIAMACHY (January 2003 - June 2004).<br />

Background Spectral measurements from<br />

satellite platforms allow to determine slant column<br />

densities of several trace gases, e.g. NO2,<br />

by applying Differential Optical Absorption Spectroscopy<br />

(DOAS). By estimating and subtracting<br />

the stratospheric column, and accounting for<br />

radiative transfer, tropospheric vertical column<br />

densities (TVCDs) can be retrieved. Time series<br />

of global NO2 TVCDs are available from the<br />

satellite instrument GOME since 1996, but the<br />

rather coarse spatial resolution of 320×40 km 2<br />

leads to a smoothed image of the spatial distribution<br />

of tropospheric NO2, often complicating<br />

the interpretation of the measurements. Since<br />

2002, spectral measurements with higher spatial<br />

resolution (60×30 km 2 ) are available from the<br />

SCanning Imaging Absorption SpectroMeter for<br />

Atmospheric CHartographY (SCIAMACHY), resolving<br />

several features of the spatial distribution<br />

of tropospheric NO2.<br />

Funding See satellite group overview.<br />

Methods and results The DOAS fit has been<br />

implemented for the evaluation of SCIAMACHY<br />

data. The processing of NO2 TVCDs is analogue<br />

to the GOME implementation.<br />

Fig. 1 shows the resulting mean of the global<br />

distribution of tropospheric NO2. Several hot<br />

spots, in particular several large cities, show up<br />

that have been smeared out in GOME data. The<br />

accurate measurement of spatial patterns allow<br />

the reliable identification of NOx sources and enables<br />

us to quantify NOx emissions as well as<br />

lifetime. Furthermore, the continuation of the<br />

GOME time series holds information on trends<br />

in emission strenghts, revealing a strong increase<br />

in China.<br />

Outlook/Future work Future improvements<br />

in DOAS fit, stratospheric estimation, radiative<br />

transfer modeling (in particular handling of<br />

clouds) will lead to high quality tropospheric data<br />

products that allow to assess several scientific<br />

questions.<br />

Main publication Beirle [2004]


74 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

2.5.3 Development of a radiative transfer model<br />

Participating scientist Tim Deutschmann, Suniti Sanghavi, Thomas Wagner<br />

Abstract A three-dimensional fully spherical Monte-Carlo model which provides realistic lightpath<br />

information in a scattering atmosphere is being implemented. The retrieved model data plays a keyrole<br />

in corect interpretation of spectroscopical measurements for estimation of spatially distributed tracegas<br />

concentrations.<br />

Figure 2.37: traced photons of λ = 411nm for a cloud layer with maximum extinction coefficient of<br />

3.5 in 3.0km altitude. Scattering events: air molecules (rayleigh, red), aerosols (mie, green) ground<br />

hits (isotropic, yellow), inter-voxel transitions (refraction, grey), TOA hit (turquoise).<br />

Background When using spectroscopy for the<br />

estimation of the amount of spatially distributed<br />

absorbing matter in the atmosphere, the information<br />

is needed, on which paths the photons of<br />

the measured spectrum propagated from the light<br />

source to the detector. The pathlengths through<br />

certain strongly absorbing regions of the atmosphere<br />

can susceptibly influence the observed intensity<br />

of the detecting instrument. Radiative<br />

transfer modelling can provide these key informations<br />

to inverting algorithms in order to retrieve<br />

spatially resolused tracegas concentrations.<br />

Existing models are limited under several points<br />

of view and cannot follow the progress in sensoring<br />

precision. Due to that the development of a new<br />

model is necessary and will also allow promising<br />

reprocessing of old data.<br />

Funding See satellite group overview.<br />

Methods and results Based on the work of<br />

Axel Morgner (2000) and mainly Christoph von<br />

Friedeburg (2003), the new program is being implemented<br />

under aspects of scalability, portability<br />

to different os and adaptability to various<br />

measurement geometries. The present algorithm<br />

uses a numerical method to generate realistic light<br />

paths in consideration of rayleigh scattering on<br />

air molecules, mie scattering on aerosols and so<br />

far isotropic ground scattering. The physically<br />

relevant properties air density, pressure, temperature,<br />

humidity, refractive index, tracegas and<br />

aerosol concentrations and ground albedo of the<br />

full spherical atmosphere are mapped into a 3D<br />

grid. Using the Backward Monte Carlo technique<br />

the simulated photons are emitted by the detector<br />

and traced through the grid until they leave the<br />

atmosphere (TOA, Figure 2.37). Then the generated<br />

paths are weighted for a certain sun position,<br />

by their possibility using a method called<br />

“forcing”.<br />

The flexibility of the new program allows the application<br />

of the model data in a wide range, not<br />

only in spectrosopy but also in atmospherical dynamics<br />

and chemistry by regarding forward traced<br />

photons, which is already possible.<br />

Outlook/Future work<br />

• more realistic mie scattering in clouds with<br />

droplet size distribution function<br />

• more realistic modellation of ground scattering<br />

by using BRDF<br />

• raman scattering and polarisation<br />

• investigation of the energy budget for certain<br />

conditions<br />

• web interface for remote model data retrieval<br />

• implementation of tomographic inversion<br />

• parallelisation<br />

Main publication von Friedeburg [2003]


2.5. SATELLITE GROUP 75<br />

2.5.4 Retrieval of methane from SCIAMACHY onboard ENVISAT<br />

Participating scientist Christian Frankenberg, Ulrich Platt, Thomas Wagner<br />

Abstract SCIAMACHY onboard ENVISAT features three near infrared spectrometers and thereby<br />

enables the retrieval of atmospheric methane with high sensitivity to the lowermost atmospheric layers.<br />

Using concurent retrievals of carbon dioxide and the application of atmospheric models, precise maps<br />

of the global distribution of column averaged methane mixing ratios are derived.<br />

Figure 2.38: Column averaged mixing ratio of methane averaged from August through November<br />

2003.<br />

Background Methane (CH4) is, after carbon<br />

dioxide, the second most important anthropogenic<br />

greenhouse gas, contributing directly 0.48 W m −2<br />

to the total anthropogenic radiative forcing of<br />

2.43 W m −2 by well-mixed greenhouse gases<br />

(IPCC, 2001). In addition, it exhibits an indirect<br />

effect of about 0.13 W m −2 through formation<br />

of other greenhouse gases, most notably<br />

tropospheric ozone and stratospheric water vapor<br />

(Lelieveld et al., 1998).<br />

A major limitation of present top-down methane<br />

emissions inventories is the limited number of atmospheric<br />

observation sites. SCIAMACHY now<br />

offers the unique possibility of sensing methane<br />

globally, retrieving methane abundances also in<br />

remote areas.<br />

Funding See satellite group overview.<br />

Methods and results An algorithm (IMAP-<br />

DOAS) was developed based on the principles<br />

of differential optical absorption spectroscopy<br />

(DOAS), that deals with the peculiarities of retrieving<br />

strong absorbers in the near infrared,<br />

thus allowing a precise retrieval of the respective<br />

trace gases. It was shown that nonlinear iterative<br />

schemes are necessary to account for saturation effects<br />

and to avoid interdependencies of spectrally<br />

overlapping strong absorbers.<br />

Global measurements of the total columns of<br />

methane with high precision were made possible<br />

by use of concurent retrievals of the relatively homogenously<br />

distributed carbon dioxide as proxy<br />

for the light path of the recorded photons. The<br />

highest abundances were found over areas of rice<br />

cultivation in South-East Asia and can be considered<br />

a direct proof of large scale methane emissions<br />

in Asia.<br />

In the time-period from August through November<br />

2003, large discrepancies between measurements<br />

and model were discovered over tropical<br />

rainforest areas. Measured abundances showed<br />

persistently higher abundances than those predicted<br />

by the model. This led to the conclusion<br />

that the tropical regions as methane source have<br />

been hitherto underestimated in curent emissions<br />

inventories.<br />

An extension of the analysis to the years 2003 and<br />

2004 showed that the discrepancies are highest<br />

during the months of August through October.<br />

The precision of these measurements now allows<br />

their use in inversion models to quantify the temporal<br />

and geographical distribution of methane<br />

sources.<br />

Main publications Frankenberg et al. [2005b],<br />

Frankenberg et al. [2005a]


76 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

2.5.5 Retrieval of carbon monoxide from SCIAMACHY onboard ENVISAT<br />

Participating scientist Christian Frankenberg, Ulrich Platt, Thomas Wagner<br />

Abstract SCIAMACHY onboard ENVISAT features three near infrared spectrometers and thereby<br />

enables the retrieval of atmospheric carbon monoxide which holds interest from several perspectives.<br />

Despite severe instrumental problems first global retrievals from SCIAMACHY have become feasible.<br />

Figure 2.39: Maximum CO vertical column densities as seen by SCIAMACHY.<br />

Background The global distribution of carbon<br />

monoxide (CO) holds interest from several perspectives:<br />

as a primary and secondary determinant<br />

of air quality, as the leading sink of hydroxyl<br />

radicals, and as an atmospheric tracer with<br />

a relatively long lifetime, that is, an indicator of<br />

how transport redistributes pollutants on a global<br />

scale. High CO concentrations can directly affect<br />

human health. Indirectly, CO plays a role in the<br />

catalytic production and destruction of ozone. In<br />

case of high NOx abundance, CO oxidation by<br />

OH radicals leads to ozone production. Global<br />

measurements with high sensitivity towards the<br />

ground are thus very valuable for the quantification<br />

of its impact on air quality and OH radical<br />

abundances.<br />

Funding See satellite group overview.<br />

Methods and results The IMAP-DOAS algorithm,<br />

which was developed at IUP Heidelberg,<br />

was applied to account for saturation effects and<br />

to avoid interdependencies of spectrally overlapping<br />

strong absorbers. Further, additional spectral<br />

calibrations for the SCIAMACHY instrument<br />

haven been elaborated to enable the retrieval from<br />

channel 8 spectra that are deteriorated due to an<br />

ice-layer and low signal to noise ratio.<br />

Since SCIAMACHY cannot be considered a dedicated<br />

greenhouse gas mission but a prototype with<br />

respect to near infrared spectroscopy, several instrumental<br />

shortcomings had to be solved. An<br />

extensive analysis of these effects enabled the retrieval<br />

of and carbon monoxide.<br />

In the retrievals, enhancements of carbon monoxide<br />

in biomass-burning regions could be clearly<br />

identified. In addition, the seasonal and geographical<br />

patterns of typical biomass burning regions<br />

could be observed. Only in the industrial regions<br />

of China, high carbon monoxide abundances were<br />

found to be persistent over the year.<br />

Main publications Frankenberg et al. [2005c],<br />

Frankenberg et al. [2005b]


2.5. SATELLITE GROUP 77<br />

2.5.6 Retrieval of cloud parameters using SCIAMACHY and GOME data<br />

Participating scientist Michael Grzegorski, Thomas Wagner, Christian Frankenberg, Mark Wenig 1 ,<br />

Nicolas Fournier 2 , Piet Stammes 2<br />

1 NASA Goddard Space Flight Center, Greenbelt, Maryland, USA<br />

2 Royal Meteorological <strong>Institut</strong>e of the Netherlands, KNMI, Utrecht, The Netherlands<br />

Abstract The retrieval of cloud parameters like cloud coverage, cloud top pressure or cloud optical<br />

thickness from satellite is an important issue both for climatology and the analysis of tropospheric<br />

trace gases. The HICRU algorithm improves retrieval of effective cloud fraction using data from<br />

SCIAMACHY on ENVISAT and GOME on ERS-2. HICRU also allows an accurate cloud retrieval<br />

over deserts, which is usually difficult for cloud algorithms.<br />

Figure 2.40: case study (08/27/2003): Results of HICRU compared with the corespondent image from<br />

Meteosat (2 hours after ENVISAT, taken from www.eumetsat.de, c○Eumetsat)<br />

Background The detection of cloud parameters<br />

like cloud coverage, cloud top pressure or<br />

cloud optical thickness from satellite is an important<br />

issue: 1.) for meteorology and the investigation<br />

of climate change and 2.) for the analysis of<br />

tropospheric trace gases from space relevant to environmental<br />

and climatological issues. Although<br />

the retrieval of different cloud parameters is useful<br />

for trace gas retrievals, especially the accurate<br />

identification of completely cloud free regions is<br />

crucial due to the shielding effect, which causes<br />

an underestimation of the vertical column density<br />

of tropospheric trace gases measured by satellite.<br />

Funding See satellite group overview.<br />

Methods and results The Heidelberg Iterative<br />

Cloud Retrieval Utilities (HICRU) retrieve effective<br />

cloud fraction by applying the widely used<br />

threshold method to the so-called Polarization<br />

Monitoring Devices (PMDs) with higher spatial<br />

resolution compared to the channels used for trace<br />

gas retrievals. The results are validated through<br />

intercomparison with different other cloud algorithms.<br />

The intercomparisons show the reliability<br />

of the HICRU algorithm. The sophisticated<br />

retrieval of the HICRU thresholds also allows an<br />

accurate retrieval over deserts, which is usually<br />

difficult for for GOME/SCIAMACHY cloud algorithms.<br />

Cloud fraction retrieved by HICRU using<br />

data both from SCIAMACHY and GOME is<br />

available free of charge on http://satellite.iup.uniheidelberg.de.<br />

Outlook/Future work The results of HICRU<br />

will be combined with the DOAS evaluation of O 2<br />

and O 4 and the results from the radiation transfer<br />

model TRACY to retrieve further cloud parameters,<br />

especially cloud top height.<br />

Main publication Grzegorski et al. [2004]


78 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

2.5.7 Satellite validation using the airborne multi axis DOAS instrument<br />

Participating scientists Klaus-Peter Heue, Thomas Wagner, Andreas Richter 2 , Marco Bruns 2<br />

Ping Wang 2 ( 2 <strong>Institut</strong> <strong>für</strong> Umweltphyisk, <strong>Universität</strong> Bremen)<br />

Abstract The Airborne Multi AXis DOAS instrument designed to separate the tropospheric from<br />

stratospheric absorptions of several Trace gases e.g. NO2. Due to the long range of the aeroplane<br />

it is ideal for validation measurements of tropospheric NO2 observed by the new satellite instrument<br />

SCIAMACHY on ENVISAT.<br />

Figure 2.41: AMAXDOAS measurements along the flight track on 19/02/2003 overlaid to SCIA-<br />

MACHY observations from the same day. The scientific SCIAMACHY data from the IUP in Bremen<br />

were taken.<br />

Background With the SCIAMACHY instruments<br />

slant and vertical columns of many trace<br />

gases can be measured. Here we concentrate on<br />

tropospheric NO2. Based on the observed spectra<br />

from SCIAMACHY several scientific DOAS<br />

products exist at different scientific groups (e.g.<br />

in Heidelberg, Bremen, Harvard). Nitrogen dioxide<br />

is known to be harmful and plays an important<br />

role in the tropospheric chemistry of ozone. Most<br />

of the tropospheric NO2 is produced by anthropogenic<br />

emissions.<br />

Funding See satellite group overview.<br />

Methods and results Tropospheric NO2 vertical<br />

and slant columns from the new satellite instrument<br />

SCIAMACHY on ENVISAT are validated<br />

by measurements of the AMAXDOAS instrument<br />

on board the DLR Falcon. The results<br />

presented here were obtained in February<br />

2003 on a flight over the Alps, the Po-Valley and<br />

the Mediterranean ( figure 2.41). Due to the<br />

similar measurement system of AMAXDOAS and<br />

SCIAMACHY both tropospheric slant and ver-<br />

tical columns can be compared. However, the<br />

stratospheric absorption has to be separated from<br />

the tropospheric signal first. In the Troposphere<br />

the local variation in the NO2 columns are very<br />

high caused by the anthropogenic emissions. The<br />

stratospheric signal shows rather smooth spatial<br />

variations. Different methods for the separation<br />

of tropospheric and stratospheric signal for both<br />

instruments were investigated. Independent information<br />

about aerosol optical thickness and mixing<br />

layer height were considered for the calculation of<br />

the AMF. The TVCD measured by AMAXDOAS<br />

varied between 16.2 and 35.2·10 15 molec/cm 2 over<br />

the Po-Valley where SCIAMACHY data resulted<br />

in 19.9 to 37·10 15 molec/cm 2 . Over less polluted<br />

areas a similarly good agreement was found. The<br />

linear correlation between the two datasets results<br />

in a slope of 0.93. The slight differences observed<br />

can be attributed to the different spatial resolution<br />

and the temporal mismatch between the measurements<br />

over the Po-Valley.<br />

Main publications Heue [2005], Heue et al.<br />

[2005]


2.5. SATELLITE GROUP 79<br />

2.5.8 Analysis of global long-term tropospheric and stratospheric BrO<br />

from GOME measurements<br />

Participating scientist Jens Hollwedel, Thomas Wagner, Roland von Glasow, Lars Kaleschke 2 ,<br />

William Simpson 3 , Ulrich Platt ( 2 University of Bremen, 3 University of Alaska)<br />

Abstract BrO leads to ozone depletion, both in the stratosphere and troposphere. The global<br />

distribution and yearly cycle of stratospheric and tropospheric BrO has been analysed. Transport<br />

events and an increase in tropospheric source strength have been discussed.<br />

Figure 2.42: Global mean BrO distribution derived from GOME for the time period 1996 - 2001.<br />

Background The importance of BrO for the<br />

ozone depletion in the stratosphere is well known.<br />

BrO can also be liberated by heterogenous reactions<br />

on the surfaces of halogen rich aerosols, especially<br />

over the one year old sea ice. This mechanism<br />

is known as the Bromine explosion leading<br />

to the tropospheric ozone hole in polar spring.<br />

Funding See satellite group overview.<br />

Methods and results Column densities of<br />

bromine monoxide have been derived from GOME<br />

for the time period from 1996 to 2001 on a global<br />

scale. Two methods for the separation of the<br />

stratospheric and tropospheric fractions of the total<br />

column density have been used (a fixed SZA<br />

interval and a reference site method). The average<br />

stratospheric BrO load has increased slightly<br />

during the time period under investigation. Investigation<br />

of sources and source strengths of boundary<br />

layer BrO show that enhanced boundary layer<br />

BrO is released in bromine explosion events during<br />

polar spring leading to tropospheric ozone holes.<br />

The sea-ice and especially frost flowers are the<br />

sources for these events. The area covered by<br />

’clouds’ of enhanced BrO in the northern hemisphere<br />

has increased by about 10% per year from<br />

1996 to 2001. Thus the source strength has increased<br />

which is probably due to changes in the<br />

Arctic sea-ice cover. Strong evidence for a free<br />

tropospheric BrO background of about 2pptv BrO<br />

in the free troposphere with a lower boundary of<br />

its lifetime of about four days has been gathered.<br />

Transport events of polar tropospheric Bro towards<br />

mid-latitudes and into the free troposphere<br />

have been discovered.<br />

Outlook/Future work A corelation analysis<br />

of stratospheric BrO and NO2 will be performed<br />

discussing the stratospheric yearly cycle of BrO.<br />

Transport events from the polar troposphere towards<br />

mid-latitudes and into the free troposphere<br />

will be further investigated.<br />

Main publication Hollwedel et al. [2004],<br />

Hollwedel [2005]


80 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

2.5.9 Enhanced SO2 Column Densities Observed Over South East Asian<br />

Region: Consequence of El Niño<br />

Participating scientist M. F. Khokhar<br />

Abstract Changes in the global atmospheric circulation patterns caused by El Niño bring about<br />

weather extremes in various parts of the world. Especially, inhibiting rainfall over the western pacific<br />

equatorial region, resulting in a lot of biomass burning events and droughty conditions. GOME data<br />

showed enhanced SO2 column densities over South East Asian region which strongly corelate to the<br />

strong El Niño event in the year 1997-98.<br />

Figure 2.43: Comparison of monthly mean maps of fire data (ATSR fire counts /pixel), in the left<br />

panel, GOME SO2 SCDs (centre) and HCHO SCDs (right panel) for the month of September from<br />

1996 to 1998. The HCHO and SO2 emissions over S.E. Asia resulted from relatively enhanced Biomass<br />

burning events as consequences of strong El Niño 1997-98 in this region. The GOME observations are<br />

averaged on a 0.5 ◦ latitude/longitude grid.<br />

Background The satellite remote sensing provides<br />

information about various atmospheric trace<br />

gas emissions and their distribution on a global<br />

scale. Sulfur Dioxide (SO2) is an important trace<br />

gas in the atmosphere. It is released to the troposphere<br />

from both human activities and natural<br />

sources (mainly from volcanic eruptions and<br />

Biomass burning). We investigated the Biomass<br />

burning in S. E. Asia for the time period 1996-<br />

2001. We find an enhancement in the SO2 SCDs<br />

for the year 1997 and 98.<br />

Funding See satellite group overview.<br />

Methods and results GOME is a nadirscanning<br />

UV/Vis. spectrometer covering the<br />

wavelength range from 240nm to 790 nm. A key<br />

feature of GOME is its ability to detect, besides<br />

ozone, several chemically active atmospheric trace<br />

gases such as SO2, CH2O NO2, BrO etc. From the<br />

ratio of earthshine radiance and solar iradiance<br />

measurements, slant column densities (SCDs) of<br />

the respective absorbers can be derived by applying<br />

the technique of differential optical absorption<br />

spectroscopy (DOAS). Satellite remote sensing is<br />

a power full tool along with several advantages<br />

over the conventional measurement techniques.<br />

Especially, to monitor the volcanic eruptions and<br />

biomass burning events resulting from forest fire<br />

which very often occur in remote and inaccessible<br />

area. Biomass burnings are also an important<br />

source of tropospheric NO2 and HCHO, results<br />

compared with SO2 column densities showed a<br />

good agreement (see figure). Enhanced SO2 SCDs<br />

for 1997 and 98 over S. E Asian region are coupled<br />

to El Niño consequences. Satellites provide<br />

the best opportunity to quantify the impact of<br />

biomass burning on global atmospheric chemistry.<br />

Outlook/Future work Synergistic use of<br />

satellite observations for different trace gases e.g.<br />

HCHO and NO2 and CO, from biomass burning<br />

and to compare their results.<br />

Main publication Khokhar et al. [2005]


2.5. SATELLITE GROUP 81<br />

2.5.10 Retrieving vertical profiles of stratospheric trace gases from satellite<br />

observations<br />

Participating scientist Sven Kühl, Janis Pukite, Thomas Wagner, and Walburga Wilms-Grabe<br />

Abstract Vertical profiles of ozone, NO2, BrO and OClO were retrieved from measurements of<br />

SCIAMACHY in limb geometry. The retrieved profiles were compared to balloon measurements and<br />

SCIAMACHY products from other institutes.<br />

Figure 2.44: Averaging kernels for typical retrievals, revealing the altitude range for which information<br />

on the trace gas distribution can be retrieved.<br />

Background It is well established that the major<br />

cause for the ozone hole, the massive depletion<br />

of ozone in the polar lower stratosphere<br />

in springtime, is the heterogeneous processing of<br />

chlorine species during polar winter, the stratospheric<br />

chlorine activation. Despite their immense<br />

effect on the ozone layer, daily and global measurements<br />

of active chlorine compounds like ClO<br />

and ClOOCl are rare. On the other hand, chlorine<br />

dioxide (OClO), an important indicator for<br />

chlorine activation, can be measured by remote<br />

sensing methods more easily than ClO or ClOOCl.<br />

GOME measurements of OClO have been applied<br />

in the long term monitoring of stratospheric chlorine<br />

activation [Wagner et al. , 2001] as well as<br />

in case studies [Kühl et al. , 2004; Richter et al. ,<br />

2005]. However, the interpretation of column densities<br />

(obtained from observations in nadir geometry)<br />

in many cases has to remain on a qualitative<br />

level, while the knowledge about 3-dimensional<br />

trace gas distributions allows also quantitative<br />

studies. Thus, the vertical profiles of ozone, NO2,<br />

BrO and OClO, retrieved from the SCIAMACHY<br />

limb measurements, will lead to a better understanding<br />

of processes relevant for polar ozone loss<br />

and can be applied for investigating contemporary<br />

open questions of stratospheric chemistry.<br />

Funding See satellite group overview.<br />

Methods and results For the retrieval of the<br />

vertical trace gas profiles a two step approach is<br />

used: First, SCDs as function of tangent height<br />

are determined by DOAS, then inversion to profiles<br />

by applying the box AMFs calculated by<br />

RTM. This two step approach enables us to study<br />

separately the impact of spectroscopy and radiative<br />

transfer modeling on the retrieved profile.<br />

The retrieved profile is always a combination of<br />

the measured SCDs, the measurement eror, the<br />

applied AMFs, and the a priori. Therefore, the<br />

retrieved SCDs and the calculated AMFs should<br />

be of little uncertainty. Also, the a priori should<br />

describe the mean value and the variance of the<br />

state to be retrieved as good as possible. The last<br />

point is especially important for species with a<br />

strong annual or diurnal cycle, like e.g. OClO.<br />

First results are in good agreement with expectations<br />

from stratospheric chemistry, as well as<br />

the seasonal and latitudinal dependency of the respective<br />

trace gas abundances. Also, first comparisons<br />

with other profile retrievals from SCIA-<br />

MACHY limb measurements [Kühl et al. , 2005]<br />

and with balloon borne observations [Butz et al.<br />

, 2005] are very promising. The averaging kernels<br />

of our NO2, BrO and OClO retrieval algorithms<br />

(shown in 2.44) reveal that information about the<br />

vertical profile can be obtained for NO2 in the altitude<br />

range from 15-40 km, for BrO from 15-28<br />

km and for OClO from 15-25 km. The vertical<br />

resolution of the retrieved profile in this altitude<br />

range is 3 km.<br />

Outlook/Future work Improving the profile<br />

retrieval in terms of spectroscopy, radiative transfer<br />

simulation and inversion approach. Application<br />

of the retrived profiles in scientific studies on<br />

open questions of stratospheric chemistry.<br />

Main publication Kühl [2005]


82 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

2.5.11 Comparison of OClO nadir measurements from SCIAMACHY and<br />

GOME<br />

Participating scientist Sven Kühl, Walburga Wilms-Grabe, Thomas Wagner<br />

Abstract Total columns of OClO were retrieved from SCIAMACHY nadir observations and compared<br />

to the longterm dataset of GOME, the predecessor of SCIAMACHY. The retrieved SCDs are<br />

in good qualitative and quantitative agreement.<br />

Figure 2.45: Maximum OClO SCD at SZA = 90 ◦ for the southern hemisphere derived from SCIA-<br />

MACHY measurements during May to October 2003 and 2004 in comparison to the coresponding<br />

minimum and maximum values derived from GOME measurements during 1996 to 2001.<br />

Background In the polar winter, temperatures<br />

inside the polar vortex can drop below the threshold<br />

for formation of polar stratospheric clouds<br />

(PSCs) which is e.g. 195 K at an altitude of approx.<br />

19 km. Heterogeneous reactions on PSCparticles<br />

convert the ozone-inert chlorine reservoirs<br />

(mainly ClONO2 and HCl) into ozone destroying<br />

species (active chlorine, mainly Cl, ClO<br />

and ClOOCl), see e.g. Solomon [1999]. This<br />

chlorine activation is the prerequisite for massive<br />

ozone destruction by catalytic cycles. ClO (chlorine<br />

monoxide) absorbs strongly at wavelengths<br />

below 310 nm, which is in the region where also<br />

the strong ozone absorptions of the Hartley bands<br />

are situated. Therefore, the absorption by ClO<br />

is masked by the much stronger O3 absorption<br />

and unambiguous detection of stratospheric ClO<br />

by UV-Spectroscopy was not possible so far. On<br />

the other hand, OClO (chlorine dioxide) shows<br />

strong differential absorption features in the spectral<br />

range from 280 to 450 nm, and therefore can<br />

be detected by means of DOAS.<br />

Funding See satellite group overview.<br />

Methods and results For the OClO DOAS<br />

analysis of SCIAMACHY spectra we use the<br />

wavelength range from 363 to 391 nm, the same as<br />

for GOME. Included reference spectra are: OClO,<br />

NO2, O3, O4, Ring, and the Eta and Zeta Spectrum<br />

(from calbration key data) for corection of<br />

polarisation features. From various tests it turned<br />

out that the inclusion of the polarisation corection<br />

spectra is essential for a corect retrieval of OClO.<br />

Other parameters that were tested are the wavelength<br />

range used for the analysis, the degree of<br />

the polynomial, and the inclusion of the reciprocal<br />

of the Fraunhofer Reference (1/I0) in the fit.<br />

While the OClO fit converges for different wavelength<br />

ranges, we finally chose the same fit window<br />

as for GOME, for reason of consistency. The<br />

OClO SCDs derived from SCIAMACHY spectra<br />

by the DOAS method are consistent with expectations<br />

from stratospheric chlorine chemistry.<br />

Large OClO SCDs are observed only for regions<br />

inside the polar vortex, their magnitude is in good<br />

agreement with independent measurements from<br />

GOME, see Figure.<br />

Outlook/Future work Improvement of retrieval,<br />

monitoring of chlorine activation, case<br />

studies (e.g. mountain wave-induced chlorine activation).<br />

Investigating OClO photochemistry by<br />

combination of measurements in limb, nadir and<br />

occultation geometry.<br />

Main publication Kühl et al. [2005]


2.5. SATELLITE GROUP 83<br />

2.5.12 Identification of tropospheric emissions sources from satellite observations:<br />

Synergistic use of HCHO and NO2 trace gas measurements<br />

Participating scientist Thiery Marbach<br />

Abstract Many uncertainties remain in the distribution and characteristic of the tropospheric<br />

sources of trace gases. The satellites data sets allow to compare global trace gas maps providing<br />

unique opportunities to determine more precisely the tropospheric sources. We present case studies<br />

for combined HCHO and NO2 satellite observations, derived from GOME measurements.<br />

Figure 2.46: Case study of trace gas comparison: HCHO is produced from biogenic isoprenes and<br />

during biomass burning. Yellow box: HCHO only from isoprenes. Red box: Both, isoprenes and<br />

biomass burning. The HCHO biogenic isoprene emissions could be separated from the HCHO due to<br />

biomass burning using the NO2-fires corelation.<br />

Background We present case studies for the<br />

combined GOME observations for 1997 of HCHO<br />

SCDs and NO2 VCDs. Additional global data sets<br />

of quantities (forest fires) measured from ATSR<br />

have been compared to the tropospheric trace gas<br />

columns.<br />

Funding See satellite group overview.<br />

Methods and results The principal biomass<br />

burning areas (intense source of HCHO) can be<br />

observed in the Amazon basin region and in central<br />

Africa. Other high HCHO emissions can be<br />

corelated with climatic events like El Nino in 1997,<br />

which induced dry conditions in Indonesia causing<br />

many forest fires. Tree isoprene emissions contribute<br />

also to high HCHO concentrations especially<br />

in southeast United States, northern part<br />

of the Amazon basin, and in the African tropical<br />

rain forest region. The HCHO data can be compared<br />

with NO2 results to identify more precisely<br />

the tropospheric sources (biomass burning events,<br />

human activities). NO2 corelate with HCHO over<br />

Africa (grassland fires) but not over Indonesia<br />

(forest fires). In south America, an augmentation<br />

of the NO2 concentrations can be observed<br />

with the fire shift from the forest to grassland<br />

vegetation. So there seems to be a dependence<br />

between the NO2 emissions during biomass burning<br />

and the vegetation type (grassland or forest),<br />

which could influence the fire temperature (so the<br />

NO2 production) through parameters like vegetation<br />

density (oxidation capacity) or humidity. The<br />

NO2-fires corelation can also be an helpful tool to<br />

discriminate more precisely the part of the HCHO<br />

emissions coming from the biomass burning and<br />

the part issue from the tree isoprene emissions.<br />

This case studie is illustrated in the figure with an<br />

example over the Amazon basin (also illustrated<br />

by the work of Ulrike Reichl).<br />

Outlook/Future work The HCHO and NO2<br />

data can also be compared with SO2 results to<br />

identify more precisely the tropospheric sources<br />

(biomass burning events, human activities, additional<br />

sources like volcanoes emissions). Comparison<br />

with CH4 and CO will also be possible<br />

by using the SCIAMACHY data sets, and could<br />

contribute to the identification of sources due to<br />

biomass burning, fossil fuel combustion or agriculture.<br />

Main publication Marbach et al. [2004], Reichl<br />

[2005]


84 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

2.5.13 Trace gas profile retrieval from SCIAMACHY limb measurements<br />

Participating scientist Janis Pukite, Sven Kühl, Thomas Wagner, and Walburga Wilms-Grabe<br />

Abstract Trace gas profile retrieval of ozone, NO2, BrO and OClO is performed. This can be done<br />

in two successive steps. First, slant column densities (SCDs) of trace gas are retrieved by DOAS from<br />

SCIAMACHY measurements at different elevations. Second, profile is derived by inverting the SCDs.<br />

For that purpose radiative transfer modelling is performed.<br />

Figure 2.47: Latitudinal cross-sections of concentrations of ozone, NO2, BrO and OClO according to<br />

an orbit on 24.08.2004.<br />

Background The SCIAMACHY (Scanning<br />

Imaging Absorption Spectrometer for Atmospheric<br />

Chartography) on ENVISAT measures solar<br />

UV-VIS-NIR radiation transmitted, backscattered<br />

and reflected by the atmosphere and the<br />

ground. The limb-scanning mode (tangential<br />

view) is implemented by the instrument allowing<br />

to perform measurements at different elevation<br />

angles. In this way the atmosphere is probed<br />

at different geometrical configurations that make<br />

instrument more or less sensitive to substances located<br />

at different altitudes in the atmosphere. To<br />

connect the measurements with atmospheric profile<br />

of a trace gas the radiative transfer properties<br />

of the atmosphere should be applied.<br />

Funding See satellite group overview.<br />

Methods and results The retrieval of profiles<br />

is done in two successive steps. First, SCDs for<br />

the trace gases are derived from the SCIAMACHY<br />

limb measurements by DOAS method. In the second<br />

step the trace gases SCDs are converted into<br />

vertical concentration profiles by means of radiative<br />

transfer modelling (RTM). For the RTM the<br />

full spherical 3D model ”Tracy”, (von Friedeburg,<br />

2003) is used. Inversion is constrained by linear<br />

optimal estimation method (Rodgers, 2000).<br />

The method demonstrates possibility to retrieve<br />

trace gas concentrations for altitudes 15 - 28 km<br />

(BrO), 15 - 40 km (ozone and NO2), 15 - 25 km<br />

(OClO). There are still uncertainties in retrieval<br />

at polar regions probably caused by ozone absorption<br />

cross-section dependence from temperature<br />

or RTM shortages. Retrieved profiles of NO2 and<br />

BrO show good agreement with retrieval done by<br />

IUP Bremen and with balloon measurements for<br />

NO2.<br />

Outlook/Future work An improvement is<br />

necessary especially for measurements made at solar<br />

zenith angles ≥ 90 ◦ as well as for retrieval<br />

of BrO and OClO. Model studies should be performed.<br />

Improvement in RTM is required.<br />

Main publication Pukite et al. [2005], Butz<br />

et al. [2005]


2.5. SATELLITE GROUP 85<br />

2.5.14 Mie theory based characterization and modeling of atmospheric<br />

aerosols<br />

Participating scientist Suniti Sanghavi<br />

Abstract We have developed a Mie model to generate the single scattering properties of a particle<br />

given its size and complex refractive index. We put up a set of 24 aerosol scenarios to represent most<br />

aerosols in the atmosphere. The Mie theory can be used to simulate these scenarios and thus examine<br />

the optical behavior of most atmospheric aerosols.<br />

Figure 2.48: Phase functions of different aerosol particles<br />

Background Aerosols have gained increasing<br />

importance in atmospheric sciences due to the<br />

key role they play in regard to, amongst others,<br />

the earth’s radiative budget, convective processes<br />

and precipitation, and stratospheric chemistry<br />

leading, eg., to the formation of the ozone<br />

hole. They remain, however, difficult to quantify<br />

due to their varied sources, lifetimes and transport<br />

mechanisms. Thus they may occur over land or<br />

water surfaces and at different heights in the atmosphere.<br />

They also display inherent variations<br />

in size, shape and chemical composition, leading<br />

to different optical properties. We classify aerosols<br />

to represent most situations found in the atmosphere<br />

and characterize their optical properties<br />

using the Mie theory. This can be used to simulate<br />

the radiative properties of aerosols occuring in nature.<br />

We intend to use the TRACY MC RTM for<br />

this purpose. This should especially help quantify<br />

the radiative effects of aerosols on the retrieval of<br />

trace gas species from the satellite DOAS instrument<br />

SCIAMACHY. Work is ongoing for other<br />

applications that may include, in conjunction with<br />

aerosol climatologies now available at sites such<br />

as AERONET, aerosol inversion products from<br />

SCIAMACHY radiances.<br />

Funding See satellite group overview.<br />

Methods and results We have adapted a compilation<br />

of 24 distinct aerosol scenarios, consisting<br />

of 5 main aerosol types, viz. urban industrial,<br />

biomass burning, desert dust, marine and<br />

volcanic, each associated with a typical complex<br />

refractive index and vertical profile. Each is further<br />

subclassified according to coarseness, absorptivity,<br />

nonsphericity or height of occurence in the<br />

atmosphere(km a.s.l.).<br />

We obtain the optical properties, viz. extinction<br />

cross section, single scattering albedo and phase<br />

function of an aerosol particle of given size and<br />

complex refractive index, using the Mie theory<br />

(See figure). The Mie theory is a special case<br />

of the Maxwell equations with boundary conditions<br />

given by the interaction of electromagnetic<br />

radiation of given wavelength at the surface of a<br />

spherical particle.<br />

Using the characteristic complex refractive indices,<br />

size distributions and vertical profiles provided<br />

by the the scenarios mentioned above, we<br />

can use the Mie theory to determine bulk properties,<br />

e.g. the Aerosol Optical Thickness (AOT)<br />

at a given location. Adding surface reflection,<br />

Rayleigh scattering, and molecular absorption allows<br />

us to simulate fluctuations in radiances measured<br />

by satellite due to variations in the aerosol<br />

loading of the atmosphere.<br />

Outlook/Future work Implementing aerosols<br />

in TRACY RTM (Quantification of the effect<br />

of aerosols on SCDs/AMFs in different spectral<br />

regions), Aerosol retrieval/inversion from satellite/ground<br />

based measurements.<br />

Main publication Sanghavi [2003]


86 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

2.5.15 Satellite observations of the global water vapor distribution<br />

Participating scientist Thomas Wagner, Steffen Beirle, Michael Grzegorski<br />

Abstract From modern UV/vis satellite instruments, the integrated water vapor concentration<br />

(often refered to as vertical column density or total column precipitable water) can be observed on<br />

a global scale. In contrast to previous satellite observations in the infrared and microwave spectral<br />

range our observations include both ocean and land surfaces with similar sensitivity.<br />

Figure 2.49: Global anomalies of the water vapor distribution during the strong ENSO event in<br />

1997/98.<br />

Background Atmospheric water vapor is the<br />

most important greenhouse gas contributing<br />

about 2/3 of the natural greenhouse effect. In<br />

contrast to other greenhouse gases like CO2 and<br />

CH4 it has a much higher temporal and spatial<br />

variability. The corect understanding and assessment<br />

of atmospheric water vapor with respect to<br />

the Earths energy budget is further complicated<br />

by its role in cloud formation and transport of<br />

latent heat. Today, many details of how the hydrological<br />

cycle reacts to climate change (water<br />

vapor feedback) are still not understood. Especially<br />

for the tropics, which contribute strongest<br />

to the water vapor greenhouse effect, the strength<br />

of the water vapor feedback is under intense debate.<br />

In our studies we investigate the dependence<br />

of the global distribution of water vapor on surface<br />

temperature. Particular studies focussed on<br />

the response to the strong ENSO in 1997/98 and<br />

on the trends from 1996-2003.<br />

Funding See satellite group overview.<br />

Methods and results The GOME instrument<br />

is one of several instruments aboard the European<br />

research satellite ERS-2. It consists of a set of four<br />

spectrometers that simultaneously measure sunlight<br />

reflected from the Earth’s atmosphere and<br />

ground in total of 4096 spectral channels covering<br />

the wavelength range between 240 and 790 nm<br />

with moderate spectral resolutions. The satellite<br />

operates in a nearly polar, sun-synchronous orbit<br />

at an altitude of 780 km with an equator crossing<br />

time at approximately 10:30 local time. The<br />

Earth’s surface is totally covered within 3 days,<br />

and poleward from about 70 latitude within 1 day.<br />

Our water vapor algorithm is based on Differential<br />

Optical Absorption Spectroscopy (DOAS)<br />

performed in the wavelength interval 611-673 nm.<br />

It consists of three basic steps (described in detail<br />

in Wagner et al. [2003]): in the first step, the spectral<br />

DOAS fitting is caried out, taking into consideration<br />

cross sections of O2 and O4 in addition<br />

to that of water vapor. From the DOAS analysis,<br />

the water vapor slant column density (the<br />

concentration integrated along the light path) is<br />

derived. In the second step, the water vapor slant<br />

column density is corected for the non-linearity<br />

arising from the fact that the fine structure water<br />

vapor absorption lines are not spectrally resolved<br />

by the GOME instrument. In the last step, the<br />

corected water vapor slant column density is divided<br />

by a ’measured’ air mass factor which is<br />

derived from the simultaneously retrieved O4 or<br />

O2 absorptions [Wagner et al., 2003, 2005b,b].<br />

Outlook/Future work The work will be continued<br />

by applying the method to new satellite<br />

instruments like SCIAMACHY and the GOME-<br />

2-series. It can be expected that the time series<br />

can be continued until 2020.<br />

Main publication Wagner et al. [2003], Wagner<br />

et al. [2005a], Wagner et al. [2005b]


2.5. SATELLITE GROUP 87<br />

2.5.16 Analysis of MAXDOAS observations in various observing geometries<br />

Participating scientist Thomas Wagner, Nicole Bobrowski, Barbara Dix, Erna Frins, Ossama<br />

Ibrahim, Roman Sinreich<br />

Abstract MAX-DOAS measurements were caried out at various locations including ship borne<br />

measurements. Sophisticated analysis strategies were developed which can yield vertical profiles not<br />

only of the trace gases of interest, but also of aerosol properties. In addition, a new tomographic<br />

MAX-DOAS technique was developed which allows to determined three-dimensional trace gas fields.<br />

Figure 2.50: General dependence of the measured O4 absorption on various parameters of MAXDOAS<br />

observations. From MAXDOAS O4 measurements, the atmospheric aerosol properties can be derived<br />

(Wagner et al., 2004)<br />

Background The Multi AXis Differential Optical<br />

Absorption Spectroscopy (MAX-DOAS) technique<br />

allows to separate the absorptions taken<br />

place at different altitudes in the atmosphere by<br />

observing scattered sun light from a variety of<br />

viewing directions. This is possible because for<br />

most measurement conditions, the observed light<br />

is scattered in the free troposphere. Thus air<br />

masses located close to the ground are traversed<br />

on a slant absorption path determined by the<br />

viewing direction; in contrast, stratospheric air<br />

masses are traversed on a slant absorption path<br />

determined by solar zenith angle. In addition to<br />

the partial columns of various trace gases (like<br />

NO2, BrO, HCHO, etc.) also information on the<br />

aerosol profile can be retrieved (see figure).<br />

Funding See satellite group overview.<br />

Methods and results MAX-DOAS observations<br />

were caried out during coordinated compar-<br />

ison campaigns at Milano (September 2003) and<br />

Cabauw (July 2005). In addition, permanent instruments<br />

are installed at Paramaribo (Suriname)<br />

since 2002. MAXDOAS observations were also<br />

caried out during several cruises of the German research<br />

vessel Polarstern. Thes observations were<br />

used for the validation of the SCIAMACHY instrument<br />

on board of the European research satellite<br />

ENVISAT. In addition to the classical MAX-<br />

DOAS geometry, also MAX-DOAS observations<br />

of sun-illuminated targets were proposed (Frins<br />

et al., 2005). Thus measurements over well defined<br />

light paths are possible which will allow tomographic<br />

inversion of horizontal gradients.<br />

Outlook/Future work The full potential of<br />

the various MAXDOAS geometries will be further<br />

examined. Inversion schemes for trace gas<br />

and aerosol profiles will be optimised.<br />

Main publication Wagner et al. [2004]


88 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

2.5.17 Comparison of Radiative Transfer Models<br />

Participating scientist Thomas Wagner, Barbara Dix, Tim Deutschmann, Klaus-Peter Heue,<br />

Suniti Sanghavi<br />

Abstract For the interpretation of UV/vis remote sensing observations from different platforms<br />

(ground, aircraft, satellite) the atmospheric radiative transfer has to be numerically modeled. In June<br />

2005 a workshop was held at Heidelberg in order to compare the various models developed in different<br />

international research groups.<br />

Figure 2.51: MAXDOAS Box AMF for an elevation angle of 3 ◦ (360nm, no aerosol).<br />

Background During recent years the requirements<br />

on numerical models for the simulation of<br />

the atmospheric radiative transfer have been substantially<br />

increased. This is first, because complex<br />

measurement geometries have evolved, like<br />

e.g. Multi-Axis-(MAX-) DOAS observations or<br />

satellite observations over a large ground pixel.<br />

Since on the other hand, computer power has<br />

also largely increased, today’s radiative transfer<br />

models often include three dimensions and<br />

can describe complex geometries. The Heidelberg<br />

radiative transfer workshop compared Boxair<br />

mass factors (AMF) and normalised radiances<br />

for MAXDOAS geometries for various aerosol scenarios.<br />

Funding See satellite group overview.<br />

Methods and results The Heidelberg RTM<br />

workshop focused on the comparison of the results<br />

of curent RTM for DOAS observations of<br />

scattered radiation. The main focus was the modeling<br />

of various MAXDOAS geometries. Accurate<br />

modeling of MAXDOAS observations is important<br />

for satellite observations because of two<br />

main reasons: first, from the radiative transfer<br />

modeling of the rather complex MAXDOAS geometries,<br />

important and detailed conclusions on<br />

the quality of the different models can be drawn.<br />

These conclusions can be directly applied to the<br />

various satellite viewing geometries. Second, accurate<br />

atmospheric trace gas products are very<br />

important for the validation of satellite measurements,<br />

especially for tropospheric trace gases. Besides<br />

the normalise radiances, also Box-AMF for<br />

various altitudes were compared (see Figure). In<br />

general, good agreement was found. However, also<br />

discrepancies were detected, some of which could<br />

be related to the treatment of sphericity. More<br />

details on the selected comparison exercises and<br />

results can be found at http://satellite.iup.uniheidelberg.de/.<br />

Outlook/Future work Further improvements<br />

of the various model results is foreseen for the near<br />

future. Additional exercises were already selected<br />

to investigate specific dependencies like the influence<br />

of the aerosol phase function and the ground<br />

albedo. It is planned to publish the results.<br />

Main publication ACCENT [2005]


2.5. SATELLITE GROUP 89<br />

2.5.18 GOME observations of stratospheric trace gas distributions during<br />

the split vortex event in the Antarctic winter 2002<br />

Participating scientists: Walburga Wilms-Grabe, Steffen Beirle, Sven Kühl, Ulrich Platt, and<br />

Thomas Wagner<br />

Abstract In the austral winter/spring 2002, an unusual major stratospheric warming led to an early<br />

split of the south polar vortex, combined with a partly filling up of the Antarctic ozone hole. This<br />

study is dealing with distributions of ozone related trace gases (O3, NO2 and OClO) measured by<br />

GOME during the split vortex event.<br />

GOME O 3, 2002/09/27<br />

500 ><br />

DU<br />

450<br />

400<br />

350<br />

300<br />

250<br />

200<br />

150<br />

100<br />

ESA / DLR / IUP Bremen eichmann@iup.physik.uni-bremen.de <<br />

Figure 2.52: O3, NO2 and OClO-distributions above the south pole at 27 Sep. 2002, measured by<br />

GOME, retrievals of IUP Bremen (O3) and IUP Heidelberg (NO2, OClO).<br />

Background Unusual high activity of planetary<br />

waves in the southern hemisphere led to the<br />

early weakening and splitting of the south polar<br />

vortex in winter/spring 2002 and strongly affected<br />

also chemical conditions in the Antarctic atmosphere.<br />

This could be clearly seen from the premature<br />

break up of the ozone hole in the last third<br />

of September [Richter et al., 2005]. The stratospheric<br />

ozone chemistry is related to the nitrogen<br />

and to the halogene chemistry. Therefore, it<br />

is of interest to investigate the evolution of O3,<br />

NO2 and OClO during this abnormal situation,<br />

whereas OClO serves as indicator for the degree<br />

of stratospheric chlorine activation.<br />

Funding See satellite group overview.<br />

Methods and results The stratospheric ozone<br />

chemistry is closely connected to shape and<br />

strength of the vortex. Therefore, the polar<br />

ozone distribution reproduces precisely the actual<br />

state of the vortex. The break up starts at Sep.<br />

21st/22nd. Simultaneously with the weakening of<br />

the ozone hole NO2 is increasing inside the vortex.<br />

At 26/27 Sep. NO2 shows unusual high<br />

SCDs above the pole, although the ozone concentration<br />

is still relatively low in the same area<br />

(see figure). As well dynamical as chemical processes<br />

can be responsible for the increased NO2<br />

concentrations. One important aspect is the vertical<br />

misalignment and realignment of the vortex<br />

during the weakening period. Also thermal decay<br />

and rapid photolysis of NO2 reservoirs of warm<br />

mid-latitude air transported to polar regions may<br />

contribute to the NO2-enrichment. OClO evinces<br />

high chlorine activation inside the vortex at 20<br />

Sep. and is rapidly decreasing after 22 Sep. At 27<br />

Sep. GOME does not find OClO any more (figure).<br />

Even after the re-establishing of one vortex<br />

fragment by mid October over the pole no OClO<br />

was observed. The rapidity of the OClO reduction<br />

in the austral spring 2002 is anomalous. In<br />

contrary to the north pole where high yearly variability<br />

of OClO is typical, the chlorine activation<br />

above the south pole varies only slightly from year<br />

to year. In the year 2002 however the decrease of<br />

OClO starts about 10 days earlier as usual and<br />

continues for approximately 7 days only.<br />

Outlook/Future work Including measurements<br />

of polar stratospheric clouds (e.g. from<br />

ENVISAT-MIPAS) and limb observations of different<br />

trace gases by SCIAMACHY during the<br />

split vortex event can provide new insights in the<br />

chemical and dynamical interactions also with vertically<br />

resolved information.<br />

Main publication Wilms-Grabe et al. [2004],<br />

Richter et al. [2005]


90 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

2.5.19 Comparison of GOME NO2 retrievals analysed by different scientific<br />

groups<br />

Participating scientists: Walburga Wilms-Grabe, Steffen Beirle, Randall Martin, Andreas Richter,<br />

Michel van Roozendael, and Thomas Wagner<br />

Abstract In order to improve nonuniform GOME NO2 products of differing analysis tools applied<br />

at several institutes, NO2 SCDs have been compared for selected GOME orbits. The results show<br />

principal agreement between retrievals of IASB in Brussels, IUP Bremen and IUP Heidelberg, but in<br />

some extent clear discrepancies to retrievals of Dalhousie University in Halifax.<br />

Figure 2.53: NO2 SCDs of one GOME orbit crossing north-east of the United States and the Pacific,<br />

analysed for 03 February 1996 (left) and 06 February 2000 (right) by Heidelberg (blue), Bremen<br />

(black), Brussels (green) and Halifax (red)<br />

Background Several scientific groups are occupied<br />

with the analysis of GOME trace gas measurements.<br />

In dependence of the used retrieval<br />

tools, the resulting trace gas distributions differ<br />

from each other, though they were analyzed for<br />

the same location and time. Therefore, a comparison<br />

study is performed in order to assess the<br />

discrepancies and to evaluate the reliability of<br />

GOME products. The study is concentrated on<br />

NO2, an important trace gas for both the troposphere<br />

and stratosphere. The assessment of NO2<br />

retrievals can help all GOME data users to choose<br />

the most appropriate data set and particularly<br />

helps the provider of evaluated GOME data to<br />

unify the different existing analyzing algorithms.<br />

Funding See satellite group overview.<br />

Methods and results For the whole GOME<br />

measurement period, two GOME orbits per year<br />

have been selected as case studies: one orbit in<br />

the winter time (February) and one in the summer<br />

time (July). The chosen orbits are all located<br />

above nearly the same region, including high polluted<br />

areas in north-east of the United States and<br />

clean areas above the Pacific. This choice allows<br />

to compare NO2 retrievals for the complete orbit,<br />

but also to consider separately polluted and<br />

non-polluted parts of the orbit. In order to obtain<br />

really basic information about reasons for the<br />

variability of GOME NO2 products, in a first step<br />

pure SCDs were compared.<br />

The figure shows two examples of several NO2 retrievals.<br />

The principal agreement of all participating<br />

groups is existing. However, all selected<br />

orbits indicate better agreement between the NO2<br />

distributions of Bremen, Brussels and Heidelberg<br />

and more obvious deviations in the NO2 results<br />

of Halifax. The deviations of Halifax are related<br />

as well to the absolute SCD values (positive offset)<br />

as to the scattering of the data. In the figure,<br />

the differing scatter patterns of Halifax can<br />

be seen clearly in the region between −50 ◦ and<br />

−10 ◦ latitude. Correlations between NO2 results<br />

of Bremen, Brussels and Heidelberg lie around<br />

0.97 and 0.99 in both polluted and unpolluted regions.<br />

Correlations between data of one of these<br />

groups and data of Halifax are around 0.97 in<br />

polluted areas and about 0.55 in the less NO2enriched<br />

region between −50 ◦ and −10 ◦ latitude.<br />

Outlook/Future work Level 2 data of the<br />

DLR have to be included in the comparison study.<br />

Also VCDs and air mass factors have to be considered,<br />

the number of selected orbits has to be<br />

extended.<br />

Main publication Publication is planned later<br />

on in an advanced stage of the comparison study.


2.5. SATELLITE GROUP 91<br />

References<br />

ACCENT. 2005. Workshop on Radiative Transfer Modeling, Heidelberg.<br />

Beirle, S. 2004. Estimating source strengths and lifetime of Nitrogen Oxides from satellite data. Ph.D.<br />

thesis, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />

Beirle, S., Spichtinger, N., Stohl, A., Cummins, K. L., Turner, T., Boccippio, D., Cooper, O. R.,<br />

Wenig, M., Grzegorski, M., Platt, U., & Wagner, T. 2005. Estimating the NOx produced by<br />

lightning from GOME and NLDN data: A case study in the (Gulf) of (Mexico). Atmos. Chem.<br />

Phys. Disc., 5, 11295 – 11329.<br />

Butz, A., Bösch, H., Camy-Peyret, C., Chipperfield, M., Dorf, M., Dufour, G., Grunow, K., Jeseck,<br />

P., Kühl, S., Payan, S., Pepin, I., Pukite, J., Rozanov, A., von Savigny, C., Sioris, C., Wagner, T.,<br />

Weidner, F., & Pfeilsticker, K. 2005. Inter-comparison of Stratospheric O3 and NO2 Abundances<br />

Retrieved from Balloon Borne Direct Sun Observations and Envisat/SCIAMACHY Limb Measurements.<br />

Atmos. Chem. Phys. Discuss., 5, 10747 – 10797. SRef-ID:1680-7375/acpd/2005-5-10747.<br />

Frankenberg, C. 2005. Retrieval of Methane and Carbon Monoxide using near infrared spectra recorded<br />

by SCIAMACHY onboard ENVISAT - Algorithm development and data analysis. Ph.D. thesis,<br />

<strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />

Frankenberg, C., Meirink, J. F., van Weele, M., Platt, U., & Wagner, T. 2005a. Assessing Methane<br />

Emissions from Global Space-Borne Observations. Science, 308(5724), 1010–1014.<br />

Frankenberg, C., Platt, U., & Wagner, T. 2005b. Iterative maximum a posteriori (IMAP)-DOAS for<br />

retrieval of strongly absorbing trace gases: Model studies for CH4 and CO2 retrieval from near<br />

infrared spectra of SCIAMACHY onboard ENVISAT. Atmos. Chem. Phys., 5, 9–22.<br />

Frankenberg, C., Platt, U., & Wagner, T. 2005c. Retrieval of CO from SCIAMACHY onboard<br />

ENVISAT: detection of strongly polluted areas and seasonal patterns in global CO abundances.<br />

Atmos. Chem. Phys., 5, 1639–1644.<br />

Grzegorski, M., Frankenberg, C., Platt, U., Wenig, M., Fournier, N., Stammes, P., & Wagner, T. 2004.<br />

Determination of cloud parameters from SCIAMACHY data for the correction of tropospheric trace<br />

gases. In: Proceedings of the ENVISAT & ERS Symposium, 6-10 September 2004, Salzburg, Austria.<br />

ESA-publication SP-572, (CD-ROM).<br />

Halasia, M.-A. 2004. SMAX-DOAS observation of atmospheric trace gases on the Polarstern<br />

ANT/XX-expedition from October 2002 until February 2003. Diplomarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>,<br />

<strong>Universität</strong> Heidelberg.<br />

Heue, K.-P. 2005. Airborne multi axis DOAS instrument and measurements of two dimensional<br />

tropospheric trace gas distributions. Ph.D. thesis, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg,<br />

Germany.<br />

Heue, K.-P., Beirle, S., Bruns, M., Burrows, J. P., Platt, U., Pundt, I., Richter, A., Wagner, T., &<br />

P. Wang, P. 2004. SCIAMACHY validation using the AMAXDOAS instrument. In: Proceedings<br />

of the ENVISAT & ERS Symposium, 6-10 September 2004, Salzburg, Austria. ESA-publication<br />

SP-572 (CD-ROM).<br />

Heue, K.-P., Richter, A., Bruns, M., Burrows, J. P., v.Friedeburg, C., Platt, U., Pundt, I., Wang,<br />

P., & Wagner, T. 2005. Validation of SCIAMACHY tropospheric NO2-columns with AMAXDOAS<br />

measurements. Atmos. Chem. Phys., 5, 1039–1051.<br />

Hollwedel, J. 2005. Observations of tropospheric and stratospheric Bromine Monoxide from satellite.<br />

Ph.D. thesis, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />

Hollwedel, J., Wenig, M., Beirle, S., Kraus, S., Kühl, S., Wilms-Grabe, W., Platt, U., & Wagner, T.<br />

2004. Year-to-Year Variations of Spring Time Polar Tropospheric BrO as seen by GOME. Adv.<br />

Space Res., 34, 804–808. doi:10.1016/j.asr.2003.08.060.<br />

Khokhar, M.F., Frankenberg, C., Roozendael, M. Van, Beirle, S., Kühl, S., Richter, A., Platt, U.,<br />

& Wagner, T. 2005. Satellite observations of atmospheric SO2 from volcanic eruptions during the<br />

time period of 1996 to 2002. Adv. Space Res., 36, 879–887. doi:10.1016/j.asr.2005.04.114.


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Kühl, S. 2005. Quantifying stratospheric chlorine chemistry by the satellite spectrometers GOME and<br />

SCIAMACHY. Ph.D. thesis, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />

Kühl, S., Dörnbrack, A., Sinnhuber, B.-M., Wilms-Grabe, W., Platt, U., & Wagner, T. 2004. Observational<br />

evidence of rapid chlorine activation by mountain waves above Northern Scandinavia. J.<br />

Geophys. Res., 109. doi:10.1029/2004JD004797.<br />

Kühl, S., Wilms-Grabe, W., Frankenberg, C., Grzegorski, M., Platt, U., & Wagner, T. 2005. Comparison<br />

of OClO Nadir measurements from SCIAMACHY and GOME. J. Adv. Space Res. in<br />

press.<br />

Marbach, T., Beirle, S., Hollwedel, J., Platt, U., & Wagner, T. 2004. Identification of tropospheric<br />

emission sources from satellite observations: Synergistic use of trace gas measurements of formaldehyde<br />

(HCHO), and nitrogen dioxide (NO2). In: Proceedings of the ENVISAT & ERS Symposium,<br />

6-10 September 2004, Salzburg, Austria. ESA publication SP-572, (CD-ROM).<br />

Pukite, J., Kühl, S., Wilms-Grabe, W., von Friedeburg, C., Deutschmann, T., Sanghavi, S., Hollwedel,<br />

J., Beirle, S., Frankenberg, C., Khokhar, M. F., Grzegorski, M., Marbach, T., Kirchof, B., Kraus, S.,<br />

Platt, U., & Wagner, T. 2005. SCIAMACHYLimb Measurements as a New Tool for Stratospheric<br />

Ozone Studies. Proceedings of the int. conference ”Integrative Approaches Towards Sustainability<br />

”Sharing””, May 11 - 14, 2005. in Jurmala, Latvia. in press.<br />

Reichl, U. 2005. Ground based spectroscopic direct Sun measurements at Timon/Northeast Brazil:<br />

Comparison of tropospheric air mass pollution during the dry and rainy season. M.Phil. thesis,<br />

University of Heidelberg, Heidelberg, Germany.<br />

Richter, A., Wittrock, F., Weber., M., Beirle, S., Kühl, S., Platt, U., Wagner, T., Wilms-Grabe, W., &<br />

Burrows, J.P. 2005. GOME observations of stratospheric trace gas distributions during the splitting<br />

vortex event in the Antarctic winter 2002 Part I: Measurements. J. Atmos. Sci., 62, 778 – 785.<br />

Sanghavi, S. 2003. An efficient Implementation of the Mie Theory to investigate the influence of<br />

Aerosols on Radiative Transfer. M.Phil. thesis, University of Heidelberg, Heidelberg, Germany.<br />

Solomon, S. 1999. Stratospheric ozone depletion: A review of concepts and History. Rev. Geophys.,<br />

37(3), 275 – 316.<br />

von Friedeburg, C. 2003. Derivation of Trace Gas Information combining Differential Optical Absorption<br />

Spectroscopy with Radiative Transfer Modelling. Ph.D. thesis, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>,<br />

<strong>Universität</strong> Heidelberg, Germany.<br />

Wagner, T. 2004a. Current status and future perspectives of atmospheric trace gas observations from<br />

space. Invited talk, <strong>Institut</strong>e Colloquium, MPI Mainz, Germany.<br />

Wagner, T. 2004b. Global monitoring of atmospheric trace gases, clouds and aerosols from<br />

UV/vis/NIR satellite instruments: Currents status and near future perspectives. Invited talk, SO-<br />

LAS Science conference, Halifax, Canada.<br />

Wagner, T. 2004c. Global monitoring of atmospheric trace gases, clouds and aerosols from<br />

UV/vis/NIR satellite instruments: Currents status and near future perspectives. Invited talk,<br />

WMO/GAW Expert Workshop, Tutzing, Germany.<br />

Wagner, T. 2004d. Moderne Methoden der Satellitenbildverarbeitung: Spektroskopie, Reflektions-,<br />

Streu-, und Absorptionsprozesse. Invited talk, WMO/GAW Expert Workshop, Tutzing, Germany.<br />

Wagner, T. 2005a. 7.5-year global trends in GOME cloud cover and humidity - a signal of climate<br />

change? Invited talk, KNMI, Utrecht, The Netherlands.<br />

Wagner, T. 2005b. Troposphärische Spurengasmessungen vom Satelliten aus. Invited talk,<br />

DECHEMA, Frankfurt, Germany.<br />

Wagner, T. 2005c. Wasserdampf-Fernerkundung mit dem ERS-2/GOME Sensor und seinen Nachfolgern.<br />

Invited talk, DWD, Offenbach, Germany.<br />

Wagner, T., Leue, C., Pfeilsticker, K., & Platt, U. 2001. Monitoring of the stratospheric chlorine<br />

activation by Global Ozone Monitoring Experiment GOME OClO measurements in the austral and<br />

boreal winters 1995 through 1999. J. Geophys. Res., 106, 4971–4986.


2.5. SATELLITE GROUP 93<br />

Wagner, T., Heland, J., M., Zöger, & U., Platt. 2003. A fast H2O total column density product from<br />

GOME - validation with in-situ aircraft measurements. Atmos. Chem. Phys., 3, 651 – 663.<br />

Wagner, T., Dix, B., von Friedeburg, C., Frieß, U., Sanghavi, S., Sinreich, R., & Platt, U. 2004.<br />

MAX-DOAS O4 measurements - a new technique to derive information on atmospheric aerosols:<br />

(I) Principles and information content. J. Geophys. Res., 109(D22205).<br />

Wagner, T., Beirle, S., Grzegorski, M., Sanghavi, S., & U., Platt. 2005a. El-Niño induced anomalies<br />

in global data sets of water vapour and cloud cover derived from GOME on ERS-2. J. Geophys.<br />

Res., 110(D15104).<br />

Wagner, T., Beirle, S., Grzegorski, M., & Platt, U. 2005b. Global trends (1996 to 2003) of total<br />

column precipitable water observed by GOME on ERS-2 and their relation to surface temperature.<br />

J. Geophys. Res. (accepted).<br />

Wilms-Grabe, W., Kühl, S., Beirle, S., Platt, U., & Wagner, T. 2004. GOME observations of stratospheric<br />

trace gas distributions during the split vortex event in the Antarctic winter 2002. Pages<br />

1053–1054 of: Proceedings Quadrennial Ozone Symposium, 1-8 June 2004, Kos, Greece.


2.6. MARHAL - MODELING OF MARINE AND HALOGEN CHEMISTRY 95<br />

2.6 MarHal - Modeling of marine and halogen chemistry<br />

MarHal is an independent Junior Research Group that is funded by the Deutsche Forschungsgemeinschaft<br />

in the Emmy-Noether program. The main research foci of our group are the investigation<br />

of photochemical and microphysical processes in the troposphere, especially in the marine boundary<br />

layer using numerical models.<br />

Group members<br />

Dr. Roland von Glasow, head of group<br />

Dr. Susanne Pechtl (b. Marquart), PostDoc<br />

Matthias Piot, DEA in oceanography and meteorology, PhD student<br />

Dipl. Met. Linda Smoydzin, PhD student<br />

Figure 2.54: Overview of the research topics of MarHal.<br />

Research field Seventy percent of the Earth’s surface is covered by oceans. Particles and gases are<br />

released from the ocean and have an influence on atmospheric chemistry and climate via changes of<br />

the oxidation power of the atmosphere. Furthermore, feedbacks between chemistry and, for example,<br />

cloud microphysical properties occur, that change the albedo and therefore alter the energy budget<br />

of the Earth (e.g. sulfate and sea salt aerosol particles and their role as cloud condensation nuclei).<br />

Measurements in the marine troposphere and in seawater have shown that exchanges of climatically<br />

relevant gases like dimethyl sulfide (DMS) and non-methane hydrocarbons occur which can have a<br />

significant impact on regional and even global photochemistry and climate. Furthermore, sea salt<br />

aerosol particles are produced that contain chlorine and bromine. Numerous aerosol samples have<br />

shown that marine aerosol is depleted in bromine compared to sea water. Once released to the gas<br />

phase bromine participates in ozone destruction cycles and also oxidizes dimethyl sulfide (DMS).<br />

Iodine is being released via biological processes in dramatic amounts from several coastal regions but<br />

also from the open ocean. Iodine is very efficient in destroying ozone and if concentrations of iodine<br />

oxides are high enough, new particle formation can occur.<br />

The role of halogens in tropospheric chemistry is not restricted to the marine environment. Very<br />

high mixing ratios of the radical bromine oxide have been measured during strong surface Ozone<br />

Depletion Events in polar regions in springtime and over saltlakes. In the Arctic BrO has also been<br />

implicated in so-called Mercury Depletion Events with an increase in the deposition of bioavailable,<br />

toxic mercury. Various measurements indicate that there is a significant background of the bromine


96 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

oxide radical in the troposphere, most likely in the free troposphere, which would significantly impact<br />

the background photochemistry in this sensitive environment (see 2.6.4).<br />

Although the mentioned domains appear to be very different they have striking similarities when<br />

halogen release and cycling are considered. This makes it feasible to address the associated research<br />

questions in one research group to benefit from synergies. Figure 2.54 shows schematically our research<br />

topics, making the interconnections more obvious.<br />

Methods Our research tools are numerical models. The main model is the one-dimensional model<br />

of the marine boundary layer MISTRA [von Glasow et al. , 2002a,b; von Glasow & Crutzen, 2004]<br />

that treats chemical processes in the gas phase, in and on aerosol particles, and cloud droplets. The<br />

microphysical module includes the growth of particles due to water vapor and uptake of other gases<br />

and a two-way feedback with radiation. Aqueous phase chemistry is calculated in sulfate and sea salt<br />

aerosol and - if a cloud is present - in cloud droplets that grew on each type of aerosol. The chemical<br />

mechanism comprises about 170 reactions in the gas phase and 270 reactions in and on aqueous<br />

particles for each of the four chemical bins. For some applications the model is run in Lagrangian box<br />

model mode where the relevant meteorological parameters (temperature, relative humidity, particle<br />

radius and liquid water content) are adjusted to the problem under investigation.<br />

We are developing an improved microphysical/microchemical module that will allow us to make<br />

more detailed studies of the microphysical (mainly growth) and chemical interactions of a particle<br />

population.<br />

Furthermore we have been using the global three-dimensional model MATCH-MPIC [Lawrence<br />

et al. , 1999; von Kuhlmann et al. , 2003] that uses meteorological data from numerical weather<br />

forecast reanalyses and allows to adjust the chemical mechanisms for the question in mind.<br />

Main activities All group members actively take part in model development and application.<br />

Polar halogen chemistry is being investigated by Matthias Piot (see 2.6.2) focusing on the effects<br />

of various chemical and meteorological parameters for the development of ozone depletion events.<br />

The effects of esp. organic surfactants on sea salt aerosol on particle growth and chemical processes<br />

like uptake or scavenging of gas phase compounds is the subject of Linda Smoydzin (see 2.6.3).<br />

Susanne Pechtl (b. Marquart) has developed and applied a parameterization for the nucleation of<br />

new aerosol particle from iodine vapors (see 2.6.1, Pechtl et al. [2005]). Data from a field campaign<br />

in Brittany (see C. Peters, Peters et al. [2005]) has been analysed with our model MISTRA. Together<br />

with Roland von Glasow she participated in a field campaign off the coast of New England on Appledore<br />

Island to collect data for the ongoing comparison and interpretation with numerical models.<br />

Currently, we are making comparisons focusing on iodine and chlorine chemistry and the effects on<br />

ozone and new particle formation (together with J. Stutz and O. Pikelnaya, Univ. of California, Los<br />

Angeles, W. Keene, Univ. Virginia, A. Pszenny, Univ. New Hampshire and other participants of the<br />

Appledore campaign). She is also developing the core routines of the new microphysical/microchemical<br />

model.<br />

The first global assessment of bromine chemistry in the free troposphere has been made by von<br />

Glasow et al. [2004] (see 2.6.4), showing that potentially very large sinks for ozone and DMS have<br />

been observed in previous studies. First comparisons with measurements are being made to help chose<br />

which model scenario fits best in the southern hemisphere (Schofield et al., in prep.).<br />

Effects of surface reactions on sea salt aerosol had been proposed in the literature to be of potentially<br />

great importance for the marine sulfur cycle, model results of Roland von Glasow showed,<br />

however, that the effects had been overestimated and are unlikely to be of importance (von Glasow<br />

2005, in prep.).<br />

A volcanic plume version of MISTRA was developed by Roland von Glasow and compared with<br />

measurements at Mt. Etna (see Bobrowski). With the help of Alessandro Aiuppa (Univ. of Palermo,<br />

Italy) several potential sets of initial plume conditions have been evaluated, showing that measurements<br />

of BrO and SO2 columns can very easily be reproduced by the model encouraging us to use<br />

the model to interpret the plume chemistry in this regard. The column densities of chlorine oxides,<br />

however, could not be reproduced satisfactorily, we did manage to reduce the mismatch from four<br />

orders of magnitude to a still very large factor of 30 (Bobrowski et al., submitted, von Glasow, in<br />

prep.).<br />

Colleagues from the National <strong>Institut</strong>e for Water and Atmospheric Research (NIWA) in Wellington,<br />

New Zealand, initiated a collaboration to investigate if observed seasonal variations in the δ 13 C concentrations<br />

as measured at their baseline station at Baring Head can be explained by known chlorine<br />

chemistry. Roland von Glasow has visited their group twice, the final model runs and a publication<br />

are in preparation.


2.6. MARHAL - MODELING OF MARINE AND HALOGEN CHEMISTRY 97<br />

Collaboration with the satellite group at the IUP include work of the detection of ship tracks in<br />

NO2 retrievals from GOME (Beirle et al. [2004]) and the spill-out of BrO from polar ODEs (Hollwedel<br />

et al., in prep., section 2.5.8).<br />

Collaborations<br />

Alfred-Wegener-<strong>Institut</strong>, Bremerhaven<br />

Cape Grim Baseline Air Pollution Station, Tasmanien, Australia<br />

Dipartimento CFTA, Università di Palermo, Italy<br />

Forschungszentrum <strong>Karls</strong>ruhe<br />

Max-Planck-<strong>Institut</strong> <strong>für</strong> Chemie, Mainz (MPI-C)<br />

National <strong>Institut</strong>e of Water and Atmospheric Research (NIWA), New Zealand<br />

National Oceanic and Atmospheric Administration, NOAA, Boulder, USA<br />

Scripps Inst. of Ocanography, University of California, San Diego (SIO), USA<br />

<strong>Universität</strong> Bremen<br />

University of California, Los Angeles (UCLA), USA<br />

University of New Hampshire, USA<br />

University of Virginia, USA<br />

Funding<br />

Deutsche Forschungsgemeinschaft, Emmy-Noether Junior Research Group MarHal<br />

Travel funds from National Science Foundation (USA), International Science and Technology<br />

Linkages Fund (New Zealand)<br />

Publications<br />

Peer Reviewed Publications<br />

1. Beirle et al. [2004]<br />

2. Fichter et al. [2005]<br />

3. Marquart et al. [2005]<br />

4. Peters et al. [2005]<br />

5. Ponater et al. [2005]<br />

6. von Glasow & Crutzen [2004]<br />

7. von Glasow et al. [2004]<br />

Grey Publications<br />

1. von Glasow [2005e]<br />

Invited Talks<br />

1. Piot & von Glasow [2005]<br />

2. von Glasow [2005f]<br />

3. von Glasow [2005d]<br />

4. von Glasow [2005c]<br />

5. von Glasow [2005b]<br />

6. von Glasow [2005g]<br />

7. von Glasow [2005h]<br />

8. von Glasow [2005i]<br />

9. von Glasow [2004a]


98 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

10. von Glasow [2004e]<br />

11. von Glasow [2004b]<br />

12. von Glasow [2004c]<br />

13. von Glasow [2004d]<br />

14. von Glasow [2005a]<br />

15. Pechtl [2005]


2.6. MARHAL - MODELING OF MARINE AND HALOGEN CHEMISTRY 99<br />

2.6.1 Modeling the possible role of iodine oxides in new particle formation<br />

Participating scientists Susanne Pechtl (b. Marquart), R. Lovejoy (NOAA), J. B. Burkholder<br />

(NOAA), and R. von Glasow<br />

Abstract The possible role of iodine oxides in new particle formation was investigated using the onedimensional<br />

marine boundary layer model MISTRA, extended by a parameterization for nucleation.<br />

While in a clean marine background atmosphere, OIO can be important for homogeneous nuclei<br />

formation, in a more polluted atmosphere it can only contribute to nuclei growth.<br />

Figure 2.55: Scetch of the scenarios: The model column is conditioned over different ennvironments<br />

and then moves over coastal regions with emissions of iodine compounds and later over the ocean.<br />

Background During the last years it became<br />

more and more evident that particle bursts observed<br />

in coastal regions were caused by iodine<br />

compounds that originate from marine alegae<br />

fields being exposed during low tide. It was suggested<br />

that nuclei may form via self-reaction of<br />

OIO, but the exact mechanism of particle formation<br />

and its atmospheric relevance is still uncertain.<br />

The 1D model MISTRA was used to exploit<br />

the nucleation potential of OIO under different environmental<br />

conditions, the importance compared<br />

to another nucleation mechanism, and the potential<br />

of OIO to contribute to the early growth of<br />

freshly nucleated particles.<br />

Funding DFG: Emmy Noether Junior Research<br />

Group MarHal Gl 353/1-1<br />

Methods and results The one-dimensional<br />

marine boundary layer model MISTRA includes<br />

chemistry in the gas and aerosol phase as well<br />

as aerosol microphysics. A two-step nucleation<br />

parameterization was implemented, where in the<br />

first step, the “real” nucleation process is parameterized,<br />

i.e., the formation of cluster-sized nuclei<br />

via condensation of gases. Both ternary sulfuric<br />

acid - ammonia - water nucleation and homomolecular<br />

homogeneous OIO nucleation were considered.<br />

For the latter, a parameterization was derived<br />

based on combined laboratory - model studies.<br />

The second step of the nucleation parameterization<br />

treats the “apparent” nucleation rate,<br />

i.e., the growth of clusters into the model’s lowest<br />

size bin by condensable vapors such as OIO.<br />

Different scenarios for a clean marine versus a<br />

polluted continental background atmosphere were<br />

compared. In every scenario, the air was assumed<br />

to move, independent of its origin, first over a<br />

coastal region (where it is exposed to fluxes of<br />

iodine compounds) and later over the open ocean<br />

(Figure 2.55).<br />

According to these sensitivity studies, in the<br />

clean marine background atmosphere OIO can be<br />

responsible for both homogeneous nuclei formation<br />

and the subsequent growth of the clusters to<br />

detectable sizes. In contrast to this, in the continental<br />

case with its higher levels of pollutants, gas<br />

phase OIO mixing ratios, and hence related nucleation<br />

rates, are significantly lower. Compared<br />

to ternary H2SO4-NH3-H2O nucleation, homogeneous<br />

OIO nucleation can be neglected for new<br />

particle formation in this case, but OIO can contribute<br />

to early particle growth, i.e., to apparent<br />

nucleation rates. In general, OIO was found to be<br />

more important for the growth of newly formed<br />

particles than for the formation of new nuclei itself.<br />

According to our studies, observations of particle<br />

“bursts” can only be explained by hot spotlike,<br />

not by homogeneously distributed emissions.<br />

Outlook/Future work The sensitivity studies<br />

were set up for ambient conditions encountered<br />

during the ICARTT 2004 field campaign. A detailed<br />

comparison with ICARTT results (regarding<br />

iodine oxides, nucleation, etc.) will be done in<br />

the future.<br />

Main publication Pechtl et al. [2005]


100 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

2.6.2 Ozone Depletion Events in the Polar Boundary Layer in Spring: A<br />

Model Study<br />

Participating scientists Matthias Piot and Roland von Glasow<br />

Abstract For more than 20 years, events with almost complete loss of ozone have been observed<br />

in the Arctic in spring. The importance of several species and meteorological parameters for these<br />

depletions have been investigated with sensitivity studies using a numerical box model.<br />

Figure 2.56: Schematic depiction of the most important processes included in the MISTRA model, applied<br />

for Arctic conditions. Fluxes over ice and sea salt production are switched ON/OFF, depending<br />

on the air composition we study.<br />

Background Reactive halogens play a major<br />

role in polar ozone depletion events (ODE): the<br />

reaction of bromine atoms with ozone, followed<br />

by the self-reaction of bromine oxides (BrO) represents<br />

a catalytic loss mechanism for ozone in the<br />

polar boundary layer (PBL). However, the triggering<br />

of the so-called ”bromine explosion” remains<br />

unclear. I present model results where prescribed<br />

bromine or chlorine fluxes are used to reproduce<br />

ODEs. I investigated the importance of several<br />

compounds for the chemistry of the PBL as well as<br />

meteorological parameters and focused on species<br />

which influence the occurrence of an ODE. This<br />

study allows us to better understand which species<br />

are important in the process of depleting ozone.<br />

Funding DFG: Emmy Noether Junior Research<br />

Group MarHal GL 353/1-1<br />

Methods and results I used the chemical and<br />

microphysical model MISTRA in the lagrangian<br />

box-model mode to study the mechanisms influencing<br />

these observed depletions in the polar<br />

boundary layer. My sensitivity studies consisted<br />

of a set of four-day runs where I changed initial<br />

mixing ratios or fluxes (or both) of 19 different<br />

species (including halogens, NOx, NOy,<br />

DMS, H2O2, HCHO...) and compared the results<br />

with base runs. The influence of temperature<br />

and humidity have also been examined. High<br />

HCHO concentrations result via increases in HO2<br />

in a redistribution of bromine species involving<br />

the aerosol phase, slowing ODEs down. Elevated<br />

DMS leads to an increase in HCHO, therefore also<br />

slowing ODEs down. By a similar production of<br />

HOx, hydrogen peroxyde (H2O2) also oxidizes Brx<br />

compounds inducing an ODE slow down. The<br />

presence of both Cl2 and Br2 in the air may lead<br />

to an unexpected decrease in the destruction process,<br />

depending on their relative mixing ratios. Increasing<br />

the mixing ratio of ethane by a factor of<br />

2 reduces the ozone mixing ratio from a partial<br />

ODE to a major ODE. For cases with low Br,<br />

ethene emphasizes the ozone loss. With high Br,<br />

it reduces the destruction process. An increase in<br />

HONO led to different eventual ozone mixing ratios,<br />

depending on its use by Brx-Clx compounds.<br />

A change in temperature or humidity modifies the<br />

liquid water content of aerosols and therefore the<br />

uptake coefficients. The recycling of halogens via<br />

the liquid phase is modified.<br />

Outlook/Future work This sensitivity study<br />

will help us investigate the potential triggers like<br />

frost flowers for the bromine explosion, using MIS-<br />

TRA in the lagrangian 1D mode.<br />

Main publication Piot and von Glasow, presentations<br />

at EGU, Vienna, 2005 and OASIS<br />

workshop, Toronto, 2005


2.6. MARHAL - MODELING OF MARINE AND HALOGEN CHEMISTRY 101<br />

2.6.3 Modeling Organic Films on Atmospheric Aerosol Particles and their<br />

Influence on Cloud Microphysics and Chemistry<br />

Participating scientists Linda Smoydzin, Roland von Glasow<br />

Abstract It is well known that organic material from the ocean’s surface can be incorporated into<br />

sea salt aerosols and that they often produce surface films. The relevance of these films for the gas<br />

phase and sea salt chemistry as well as for potential changes in the microphysical properties in cloud<br />

condensation nuclei is investigated.<br />

Figure 2.57: Daily course of aqueous phase concentration of HCl and HNO3 (black: organic free<br />

case, red: case with organics)<br />

Background In the last years more and more<br />

field experiments took place to characterize the<br />

chemical composition of sea salt aerosols but due<br />

to the large number and complexity of organic<br />

compounds it is only possible to determine functional<br />

groups present in the aerosol. Despite these<br />

uncertainties the measurements have shown that<br />

the organic mass fraction in fresh sea salt aerosols<br />

might be large enough to have a significant influence<br />

on cloud microphysics and atmospheric<br />

chemistry. It is assumed that surface-active organic<br />

matter of biogenic origin is enriched in the<br />

oceanic surface layer and gets into the atmosphere<br />

by bubble bursting. Surface active organic matter<br />

present in sea salt aerosols can lead to a decrease<br />

of the aerosol’s surface tension which reduces the<br />

mass transfer between the gas phase and liquid<br />

phase as well as water uptake into the aerosol.<br />

Funding DFG: Emmy Noether Junior Research<br />

Group MarHal GL 353/1-1<br />

Methods and results For studying the effect<br />

of organic surfactants a one-dimensional numerical<br />

model which contains a microphysics scheme<br />

and a detailed description of chemistry in the gas<br />

phase, in aerosol particles and in cloud droplets<br />

is used. Chemical composition and hygroscopic<br />

properties of aerosols are important aspects when<br />

regarding droplet formation and droplet growth.<br />

With simple assumptions simulating an organic<br />

film on the aerosol we tested how strong the influence<br />

of surfactants on cloud microphysics in<br />

our model is. The decrease in water uptake and<br />

a decreased solubility of the aerosol due to the<br />

organic mass fraction leads to an increase in the<br />

number of small aerosol particles. The observed<br />

changes in the aerosol size distribution, however,<br />

were small and might be negligible when considering<br />

droplet growth and cloud cover.<br />

Regarding the influence of organic matter on<br />

chemistry it is assumed that sea salt aerosols emitted<br />

from the ocean contain fatty acids which are<br />

known to be film forming compounds. The organic<br />

coating which hinders mass transfer between<br />

the gas and liquid phase is destroyed by reaction<br />

of the fatty acid with ozone. In fig. 2.57 the daily<br />

course of HNO3 and HCl for a three days model<br />

run is shown. Measurements have shown that an<br />

average organic mass fraction of 5-10% can be assumed.<br />

Although the organic mass fraction in this<br />

model run is less than 5% the uptake into the liquid<br />

phase is decreased as can be seen in lower<br />

concentrations in the case where organics were<br />

present in the aerosol. Coupled with the lower<br />

uptake into the liquid phase might be a change in<br />

the aerosol’s pH which also changes the chemical<br />

properties of the aerosol.<br />

Outlook/Future work Further investigation<br />

needs to be done to verify the uncertainties regarding<br />

the question of how strong the influence<br />

of organics really is and which chemical processes<br />

are affected exactly.


102 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

2.6.4 Impact of reactive bromine chemistry in the troposphere<br />

Participating scientists Roland von Glasow, R. von Kuhlmann (MPI-C), M. G. Lawrence (MPI-<br />

C), U. Platt, and P. J. Crutzen (MPI-C, SIO)<br />

Abstract The potential impact of 0.5 - 2 pmol mol −1 BrO on the photochemistry in the free<br />

troposphere was investigated with the help of a global three-dimensional transport model. Annual<br />

zonal mean ozone mixing ratios are reduced by up to 20 % pointing to a potentially very significant<br />

ozone loss process that has been ignored so far.<br />

Figure 2.58: Annually and zonally averaged ratio of O3 in a model run with bromine chemistry to O3<br />

in a run without bromine. The ordinate is the σ-level multiplied by 1000 which is approximately the<br />

pressure in hPa and the abscissa is latitude in degrees.<br />

Background Satellite observations suggest the<br />

widespread presence of BrO in the troposphere<br />

also outside the polar regions with global background<br />

vertical columns of about 1-3 × 10 13<br />

molec cm −2 , corresponding to BrO mixing ratios<br />

of 0.5-2 pmol mol −1 if uniformly mixed in the<br />

troposphere. The synopsis of the various measurmenets<br />

indicates that the tropospheric BrO<br />

was mainly located within the free troposphere<br />

(FT). The sources for reactive bromine in the free<br />

troposphere are thought to include the decomposition<br />

of organic bromine compounds, release from<br />

sea salt aerosol and upward transport, downward<br />

transport from the stratosphere, upward transport<br />

from ”ozone depletion events” in the polar<br />

boundary layers during spring (”spillout”), and<br />

release from slowly erupting volcanoes but a quantification<br />

of these processes remains to be made.<br />

Funding DFG: Emmy Noether Junior Research<br />

Group MarHal Gl 353/1-1<br />

Methods and results We used the global atmospheric<br />

chemistry transport model MATCH-<br />

MPIC and prescribed bromine sources to reproduce<br />

the observed BrO vertical columns taking<br />

inorganic gas phase chemistry and recycling on<br />

sulfate aerosol surfaces into account. Our vertical<br />

tropospheric columns are 0.3 - 2.4 x 10 13<br />

molec cm −2 corresponding to BrO mixing ratios<br />

of >0.1 to 2 pmol mol −1 . This amount of reactive<br />

bromine lead to a reduction in the zonal annual<br />

mean O3 mixing ratio of up to 18% in widespread<br />

areas, and regionally up to 40% compared to a<br />

model run without bromine chemistry. The lifetime<br />

of inorganic bromine was increased due to the<br />

recycling on sulfate aerosol and ranged from about<br />

ten days in the lower troposphere to 20 days in the<br />

upper troposphere. According to the model the<br />

changes in ozone were not only due to photochemical<br />

ozone destruction but also due to a reduction<br />

of ozone production as evident by changes in the<br />

HO2 : OH ratio that also affected the mixing ratios<br />

of NOx and PAN. Our lower limit estimate<br />

of the effect of BrO on dimethyl sulfide (DMS) in<br />

the marine boundary layer showed that the effect<br />

was even larger than on ozone, with up to 60%<br />

reduction of DMS tropospheric column. This is<br />

accompanied by dramatic changes in DMS oxidation<br />

pathways, reducing sulphate production and<br />

hence its cooling effect on climate. These results<br />

highlight a significant missing component in the<br />

tropospheric budgets of ozone and DMS.<br />

Outlook/Future work We will use our experience<br />

from the process modeling to developing<br />

parameterizations for the sources of inorganic<br />

bromine as well as a reduced reaction mechanism.<br />

Main publication von Glasow et al. [2004]


2.6. MARHAL - MODELING OF MARINE AND HALOGEN CHEMISTRY 103<br />

References<br />

Beirle, S., Platt, U., von Glasow, R., Wenig, M., & Wagner, T. 2004. Estimate of nitrogen<br />

oxide emissions from shipping by satellite remote sensing. Geophys. Res. Lett., 31, L18102,<br />

doi:10.1029/2004GL020312.<br />

Fichter, C., Marquart, S., Sausen, R., & Lee, D. S. 2005. The impact of cruise altitude on contrails<br />

and related radiative forcing. Met. Zeitsch., 14, 563 – 572.<br />

Lawrence, M. G., Crutzen, P. J., Rasch, P. J., Eaton, B. E., & Mahowald, N. M. 1999. A model<br />

for studies of tropospheric photochemistry: Description, global distributions, and evaluation. J.<br />

Geophys. Res., 104, 26245 – 26277.<br />

Marquart, S., Ponater, M., Ström, L., & Gierens, K. 2005. An upgraded estimate of the radiative<br />

forcing of cryoplane contrails. Met. Zeitsch., 14, 573 – 582.<br />

Pechtl, S. 2005. Halogenchemie in der Troposphäre: Überblick und Beispiele <strong>für</strong> Prozessstudien mit<br />

numerischen Modellen. Invited talk at the DLR, Oberpfaffenhofen, 15.11.2005.<br />

Pechtl, S., Lovejoy, E. R., Burkholder, J. B., & von Glasow, R. 2005. Modeling the possible role of<br />

iodine oxides in atmospheric new particle formation. Atmos. Chem. Phys. Discuss., 5, 9907 – 9952.<br />

Peters, C., Pechtl, S., Stutz, J., Hebestreit, K., Hönninger, G., Heumann, K. G., Schwarz, A., Winterlik,<br />

J., & Platt, U. 2005. Reactive and organic halogen species in three different European coastal<br />

environments. Atmos. Chem. Phys., 5, accepted.<br />

Piot, M., & von Glasow, R. 2005. Sensitivity studies of ODEs and frost flowers with a numerical<br />

model. Invited talk at the OASIS workshop, Toronto, Canada, 20.09.2005.<br />

Ponater, M., Marquart, S., Sausen, R., & Schumann, U. 2005. On contrail climate sensitivity. Geophys.<br />

Res. Lett., 32, L10706, doi: 10.1029/2005GL02258.<br />

von Glasow, R. 2004a. Halogenchemie in der Troposphäre - Untersuchungen mit numerischen Modellen.<br />

Invited talk at the Insitut <strong>für</strong> Meteorologie und Klimaforschung, <strong>Karls</strong>ruhe, 02.11.2004.<br />

von Glasow, R. 2004b. Links between sulfur and halogen chemistry and implications for our climate.<br />

Invited talk at the Afred-Wegener-<strong>Institut</strong> <strong>für</strong> Meeresforschung, Bremerhaven, 05.02.2004.<br />

von Glasow, R. 2004c. Modeling of halogen chemistry: Overview and impact on sulfur cycle. Invited<br />

talk at the EGU meeting, Nice, 2004.<br />

von Glasow, R. 2004d. Sea salt aerosol chemistry: Brief overview and recent modeling results. Invited<br />

talk at the AAAR meeting, Atlanta, 2004.<br />

von Glasow, R. 2004e. Tropospheric halogen chemistry and its implications for O3 and sulfur in<br />

the boundary layer and free troposphere. Invited talk at the <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, Bremen,<br />

06.02.2004.<br />

von Glasow, R. 2005a. Invited talk at the AGU meeting, San Francisco, 2005.<br />

von Glasow, R. 2005b. Halogenchemie in der Troposphäre - Untersuchungen der Wechselwirkungen<br />

mit Ozon und Schwefel in Prozess- und globalen Modellstudien. Invited talk at the <strong>Institut</strong> <strong>für</strong><br />

Troposphärenforschung, Leipzig, 12.05.2005.<br />

von Glasow, R. 2005c. Impact of bromine on tropospheric photochemistry. Invited talk at the<br />

IGAC/SPARC workshop, Mainz, 19.05.2005.<br />

von Glasow, R. 2005d. Importance of the surface reaction OH + Cl- on sea salt aerosol for the<br />

chemistry of the MBL - a model study. Invited talk at the EMSI Workshop on Ions and Molecules<br />

at Aqueous Interfaces, Prague, Czech Republic, 27.06.2005.<br />

von Glasow, R. 2005e. Lead Essay - Research Front Iodine. Env. Chem., 2, in press.<br />

von Glasow, R. 2005f. Reactive halogen chemistry in the troposphere - Using numerical models for<br />

detailed process studies of the marine boundary layer and a first global assessment. Invited talk at<br />

NIWA, Lauder, New Zealand, 15.09.2005.


104 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

von Glasow, R. 2005g. Reactive halogen chemistry in the troposphere - Using numerical models for<br />

detailed process studies of the marine boundary layer and a first global assessment. Invited talk at<br />

Harvard Univ., Cambridge, MA, USA, 08.04.2005.<br />

von Glasow, R. 2005h. Reactive halogen chemistry in the troposphere - Using numerical models for<br />

detailed process studies of the marine boundary layer and a first global assessment. Invited talk at<br />

the Univ. New Hampshire, Durham, USA, 07.04.2005.<br />

von Glasow, R. 2005i. Reactive halogen chemistry in the troposphere - Using numerical models for<br />

detailed process studies of the marine boundary layer and a first global assessment. Invited talk at<br />

the Univ. of East Anglia, Norwich, UK, 28.02.05.<br />

von Glasow, R., & Crutzen, P. J. 2004. Model study of multiphase DMS oxidation with a focus on<br />

halogens. Atmos. Chem. Phys., 4, 589 – 608.<br />

von Glasow, R., Sander, R., Bott, A., & Crutzen, P. J. 2002a. Modeling halogen chemistry in the marine<br />

boundary layer. 1. Cloud-free MBL. J. Geophys. Res., 107, 4341, doi: 10.1029/2001JD000942.<br />

von Glasow, R., Sander, R., Bott, A., & Crutzen, P. J. 2002b. Modeling halogen chemistry in the<br />

marine boundary layer. 2. Interactions with sulfur and cloud-covered MBL. J. Geophys. Res., 107,<br />

4323, doi: 10.1029/2001JD000943.<br />

von Glasow, R., von Kuhlmann, R., Lawrence, M. G., Platt, U., & Crutzen, P. J. 2004. Impact of<br />

reactive bromine chemistry in the troposphere. Atmos. Chem. Phys., 4, 2481 – 2497.<br />

von Kuhlmann, R., Lawrence, M. G., Crutzen, P. J., & Rasch, P. J. 2003. A Model for Studies of<br />

Tropospheric Ozone and Non-Methane Hydrocarbons: Model Description and Ozone Results. J.<br />

Geophys. Res., 108, 4294, doi:10.1029/2002JD002893.


2.7. CARBON CYCLE GROUP 105<br />

2.7 Carbon Cycle Group<br />

Christel Facklam (Techn.), Samuel Hammer (PhD), Renate Heinz (Techn.), Ingeborg<br />

Levin (GL), Tobias Naegler (Post Doc), Christoph Schönherr (Dipl.), Cordelia Veidt<br />

(PhD, since Oct. 2005).<br />

High precision greenhouse gases observations (CO2, CH4, N2O, H2O), together with their isotope<br />

ratios as well as related tracer (CO, H2, SF6, 222 Radon) measurements are performed on the global,<br />

continental and regional scale. These measurements are used in combination with regional and trajectory<br />

models to study respective source and sink processes and with global box models to investigate<br />

their biogeochemical cycles.<br />

Figure 2.59: Map of monitoring stations and measurement platforms where trace gas and isotope<br />

samples are collected for analysis<br />

Overarching topic: Investigation of the regional and global biogeochemical cycles of CO2, CH4,<br />

N2O and H2<br />

Background: Increasing greenhouse gases in the atmosphere are a major player in Earth climate<br />

change; quantitatively understanding the causes of this increase is an indispensable pre-requisite for<br />

future climate prognoses. The most reliable information on the bio-geochemical cycles of greenhouse<br />

gases come from long term atmospheric observations combined with modelling. The Heidelberg Carbon<br />

Cycle Group is significantly contributing to this international effort by providing unique (isotopic)<br />

measurements as well as validation tracer techniques and budget modelling.<br />

Main methods: The Group is running a high-precision gas chromatography (GC) laboratory (see<br />

Hammer, article 2.7.3, this issue) and is responsible for the stable isotope ratio mass spectrometry<br />

(IRMS) laboratory of the <strong>Institut</strong>e. Deuterium measurements in atmospheric methane samples are<br />

made by IRMS and - in addition - by Tunable Laser Spectroskopy in co-operation with the MPI<br />

<strong>für</strong> Kernphysik, Heidelberg (Prof. T. Röckmann). A unique global network for continuous 14 CO2<br />

observations is maintained in collaboration with the Radiocarbon Laboratory [Levin & Hesshaimer,<br />

2000, see also article 2.7.1 from Levin & Kromer, this issue, and section 6.1, this issue]. Atmospheric<br />

transport tracers such as 222 Radon [Levin et al. , 2002] and SF6, analysed in collaboration with the<br />

Limnology group (Ilmberger, section 4.2, this issue) are measured at global and European sites for<br />

transport model validation and source estimates with the Radon-Tracer-Method [Levin et al. , 1999].<br />

A global box model for CO2 and its isotopes was developed in the last years (Naegler, article 2.7.2,<br />

this issue) which is currently adapted for other greenhouse gases budgets as well as tracers such as<br />

Beryllium isotopes in collaboration with the Glaciology Group (Wagenbach, section 3.2, this issue).<br />

Major activities of the year: As most of our work strongly relies on the precise measurement of<br />

mixing ratios by gas chromatography, and as there was no funding available for investment of a new


106 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

instrument (the GC for greenhouse gases has been purchased in 1994 and that for CO measurements<br />

is a permanent loan from Forschungszentrum Jülich (Dr. A. Volz-Thomas)) we made a special effort<br />

to modernise and couple these two systems including completely new hard- and software for data<br />

acquisition and evaluation. This work has been finalised in 2005 (see Hammer, article 2.7.3, this issue<br />

and Schönherr [2005]) and led to a significant improvement of measurement precision in addition to<br />

the capability to now also analyse atmospheric Hydrogen mixing ratios at high precision.<br />

The scientific highlight of the last year concerns a question on which the group has worked now<br />

since more than one decade, namely quantitatively closing the global budget of bomb radiocarbon<br />

in the carbon system. The problem of a serious mismatch in the budget was first presented by<br />

Hesshaimer et al. [1994] in Nature, suggesting an over-estimate of the bomb 14 C inventory of the<br />

world oceans. This problem was furtheron discussed in the scientific literature and has now finally<br />

come to a solution after new (reduced) oceanic 14 C inventories had been published in 2004 for two<br />

points in time [Peacock, 2004; Key et al. , 2004]. In his PhD thesis, Tobias Naegler was now able<br />

to derive a quantitatively consistent bomb 14 C budget with help of the GRACE model, and could<br />

estimate the total bomb 14 C inventory in the carbon system [Naegler, 2005]. This now serves as the<br />

main tool for future modelling of 14 CO2 in the global atmosphere on the basis of our unique highprecision<br />

world-wide 14 CO2 observations (Levin and Kromer, article 2.7.1, this issue) to use 14 C as a<br />

quantitative constraint to determine exchange rates and turnover times in the global carbon cycle.<br />

Besides the projects performed by individual scientists of the group we have been part of two<br />

EU-funded projects, MethMonitEUr and TCOS-Siberia. MethMonitEUr aimed at harmonising and<br />

evaluating continuous CH4 observations in Europe which are used to determine the European budget of<br />

CH4 emissions. MethMonitEUr also supported our CH4 isotope measurements at Alert (discontinued<br />

in 2004) and Neumayer station. TCOS-Siberia aims at determining the carbon budget of Western<br />

Russia and Siberia. Here we contribute with trace gas and CO2 stable isotope measurements of flask<br />

samples collected during regular aircraft profiling at Syktyvkar (Ural Mountains) and Cherskii (Polar<br />

Eastern part of Siberia). Both projects end in 2005 but extension is applied for at the EU.<br />

How are single projects linked? Projects are linked by common measurement techniques and<br />

monitoring stations (i.e. Heidelberg, Schauinsland, Neumayer, Alert etc.). Data evaluation and<br />

interpretation on different scales is naturally linked through common source and sink distributions<br />

of the different greenhouse gases, such as biospheric, anthropogenic, chemical oxidation/destruction.<br />

Common modelling techniques and using tracers such as 222 Radon or trajectories are applied in the<br />

different projects.<br />

External Collaborations:<br />

MPI for Biogeochemistry, Jena (Prof. Martin Heimann, Dr. Armin Jordan, Dr. Ute Karstens, Olaf<br />

Kolle, Prof. Detlef Schulze, Dr. Axel Steinhof), German Umweltbundesamt (Prof. <strong>Ruprecht</strong> Schleyer,<br />

Frank Meinhardt), Forschungszentrum Jülich (Dr. Andreas Volz-Thomas), MPI <strong>für</strong> Kernphysik, Heidelberg<br />

(Prof. Thomas Röckmann), AWI Bremerhaven (Dr. Rolf Weller), Univ. Frankfurt, Inst. <strong>für</strong><br />

Meteorologie (Dr. Andreas Engel), LSCE, Gif-sur-Yvette, France, (Dr. Philippe Ciais, Dr. Martina<br />

Schmidt), Royal Holloway, Univ. of London, Egham, UK (Prof. Euan Nisbet), Meteorological Service<br />

of Canada, Toronto (Douglas Worthy), Krakow University (Prof. Kazimierz Rozanski), and many<br />

others.<br />

Funding: The scientific work of the group is mainly funded by research grants from the EU (TACOS,<br />

MethMonitEUr, TCOS-Siberia and CarboEurope-IP) and DFG (Atmospheric Radiocarbon).<br />

Publications<br />

Peer Revied Publications<br />

1. Levin & Kromer [2004]<br />

2. Röckmann & Levin [2005]<br />

Doctoral Theses<br />

1. Naegler [2005]


2.7. CARBON CYCLE GROUP 107<br />

Diploma Theses<br />

1. Schönherr [2005]<br />

2. Schell [2004]<br />

Invited Talks<br />

1. Levin [2004b]<br />

2. Levin [2004a]<br />

3. Levin [2005a]<br />

4. Levin [2005b]


108 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

2.7.1 Global long-term observations of Radiocarbon in atmospheric CO2,<br />

revisited<br />

Participating scientist Ingeborg Levin, the Radiocarbon Laboratory, Bernd Kromer<br />

Abstract A global network of high-precision atmospheric 14 CO2 observations is maintained, providing<br />

an independent constraint for carbon cycle modelling. Apart from this innovative application<br />

important in research of the anthropogenic CO2 problematic also various modern dating techniques<br />

make use of our unique 14 C records [Mayorga et al. , 2005; Spalding et al. , 2005].<br />

Figure 2.60: Observed ∆ 14 C in atmospheric CO2 and tree rings<br />

Background Initiated by the late Karl Otto<br />

Münnich, Heidelberg was among the first laboratories<br />

involved in precise long-term observations of<br />

bomb 14 C perturbations in the global carbon system.<br />

Related atmospheric 14 CO2 monitoring extended<br />

globally and carried into the present time<br />

constitutes a world-wide unique exercise [Levin<br />

& Hesshaimer, 2000]. This long-term and sometimes<br />

painful effort of the Carbon Cycle Group at<br />

IUP now offers a wealth of intriguing applications<br />

which range from environmental issues like studying<br />

global carbon cycle dynamics to life science<br />

and forensic aspects.<br />

Methods and results Continuous bi-weekly<br />

integrated CO2 samples are collected at eight<br />

globally distributed background stations as well<br />

as in Germany in the Black Forest (Schauinsland)<br />

and in Heidelberg (Schönherr, article 2.7.4, this<br />

issue) and are analysed at high precision for their<br />

14 C activity by conventional radioactive counting<br />

(Kromer, section 6.1, this issue). The long term<br />

trend of ∆ 14 C in CO2 in the Northern Hemisphere<br />

troposphere from 1959 until 2005 is displayed in<br />

Figure 2.60 [Levin & Kromer, 2004]. Due to atmospheric<br />

nuclear weapon testing in the 1950s and<br />

early 1960s the atmospheric 14 CO2 level increased<br />

by about a factor of two (∆ 14 C≈1000�) compared<br />

to the natural reference level. The present<br />

steady decline which is mainly driven by the ex-<br />

change with oceanic CO2 and by input of 14 C-free<br />

fossil fuel CO2 into the atmosphere are underlain<br />

relatively weak perturbations. These secondary<br />

variations reflect interesting processes, for example<br />

the very regular seasonal cycle of 14 CO2 at mid<br />

latitude northern hemispheric sites today (inlay of<br />

Figure 2.60) are mainly caused by stratospheretroposphere<br />

exchange and by the seasonal release<br />

of bomb 14 C stored in the biosphere for the last<br />

50 years now re-entering the atmosphere (Naegler,<br />

article 2.7.2, this issue). This recent net source of<br />

bomb 14 C to the atmosphere is also reflected in<br />

a tropical 14 CO2 maximum while a relative minimum<br />

is observed in mid-to-high southern latitude<br />

which is caused by disequilibrium fluxes between<br />

ocean surface water and the atmosphere [Levin &<br />

Hesshaimer, 2000].<br />

Outlook/Future work The small but significant<br />

signals observed in atmospheric 14 CO2 are<br />

used in combination with the GRACE model<br />

(Naegler, article 2.7.2, this issue) and more sophisticated<br />

global 3-dimensional models to put independent<br />

constraints on carbon exchange on earth.<br />

Main publication: Levin & Kromer [2004]<br />

Funding Funding: CarboEurope-IP, DFG (Atmospheric<br />

Radiocarbon).


2.7. CARBON CYCLE GROUP 109<br />

2.7.2 Simulating Bomb Radiocarbon: Implications for the Global Carbon<br />

Cycle<br />

Participating scientist Tobias Naegler, Vago Hesshaimer, Ingeborg Levin, Philippe Ciais (LSCE,<br />

Gif-Sur-Yvette, France), Keith Rodgers (LODYC, Paris, France)<br />

Abstract With the help of the two-dimensional global (radio-)carbon cycle model GRACE, we<br />

estimated the total production of bomb 14 C and simulated bomb 14 C inventories in the main carbon<br />

cycle reservoirs. Furthermore, we exploited the constraints that observed bomb 14 C inventories impose<br />

on stratosphere-troposphere and air-sea gas exchange.<br />

Figure 2.61: Observed (symbols) and simulated<br />

(lines) bomb 14 C inventories in the troposphere,<br />

stratosphere, biosphere and ocean. The black<br />

line denotes the total simulated accumulated<br />

bomb 14 C production, the black symbols the<br />

”observation-based” total inventory.<br />

Background Bomb radiocarbon has been produced<br />

in atmospheric nuclear bomb tests. It<br />

is injected mainly into the stratosphere. Oxydised<br />

to 14 CO2, it takes part in the global carbon<br />

cycle. The production of bomb radiocarbon<br />

peaks sharply in the late 1950s and early 1960s.<br />

Due to this pulse-like injection, bomb radiocarbon<br />

acts like a one-time release of a dye-tracer<br />

into the stratosphere. The analysis of the subsequent<br />

distribution of bomb 14 C in the earth system<br />

allows to constrain exchange times between<br />

the main carbon reservoirs stratosphere, troposphere,<br />

biosphere and ocean, e.g. to quantify<br />

stratosphere-troposphere exchange (STE), the atmospheric<br />

interhemispheric exchange time, air-sea<br />

gas exchange and turnover times of biospheric carbon<br />

pools.<br />

Methods and results We simulated the<br />

global bomb radiocarbon cycle with the Global<br />

RAdioCarbon Exploration model GRACE, consisting<br />

of a 22-box zonally averaged twodimensional<br />

atmosphere coupled to a well-mixed<br />

4-reservoir biosphere. Radiocarbon exchange between<br />

atmosphere and the ocean was calculated<br />

according to observed tropospheric and ocean surface<br />

∆ 14 C . The model comprises all relevant<br />

sources of radiocarbon (natural, bomb and industrial<br />

production). The seasonal air mass exchange<br />

between model boxes was calibrated with stratospheric<br />

and tropospheric 14 CO2 observations as<br />

well as tropospheric observations of SF6 and the<br />

10 Be/ 7 Be ratio. The simulated air mass transport<br />

across the tropopause then gives an estimate<br />

of the effective STE necessary to reproduce the<br />

observed tracer distributions. The total radiocarbon<br />

production by atmospheric nuclear bomb<br />

tests was determined with the help of the model<br />

and available stratospheric and tropospheric radiocarbon<br />

observations. The model simulated<br />

the distribution of bomb radiocarbon among the<br />

carbon reservoirs stratosphere, troposphere, biosphere,<br />

and ocean. Simulated bomb radiocarbon<br />

inventories turned out to be in very good agreement<br />

with all available stratospheric and tropospheric<br />

radiocarbon observations as well as with<br />

the latest estimates of the ocean bomb radiocarbon<br />

inventories during the GEOSECS and WOCE<br />

surveys [Peacock, 2004; Key et al. , 2004]. For<br />

the very first time, the GRACE model is thus capable<br />

of closing the bomb radiocarbon budget in<br />

the global carbon system. Using the available latest<br />

atmospheric and oceanic (radio-) carbon data,<br />

we developed a new, improved parameterisation<br />

of air-sea gas exchange which is easily adaptable<br />

to new estimates of the ocean bomb 14 C inventory<br />

and the global wind speeds, two significant sources<br />

of uncertainty in this approach. Furthermore, we<br />

estimated an observation-based biospheric bomb<br />

14 C inventory which can be used to constrain the<br />

setup and parameterisation of biosphere models.<br />

Outlook/Future work We will analyse in detail<br />

bomb 14 C constraints on biospheric parameters.<br />

Furthermore, the GRACE model will be<br />

improved by adding an ocean module, allowing<br />

carbon isotope simulations in the coupled<br />

atmosphere-ocean-biosphere system.<br />

Main publication: Naegler [2005]<br />

Funding This PhD thesis was a close collaboration<br />

with the LSCE, Gif-sur-Yvette, France and<br />

has been funded by the EU projects AEROCARB<br />

and CarboEurope-IP and by the DFG.


110 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

2.7.3 Coupling and modernisation of the Heidelberg Greenhouse Gases<br />

and CO - GC systems for continuous measurements<br />

Participating scientists Samuel Hammer, Christoph Schönherr, Christl Facklam, Ingeborg Levin<br />

Abstract Two separate GC instruments were combined via one sample inlet system. The data<br />

acquisition and evaluation software was modernised. In addition, it is now possible to determine<br />

molecular hydrogen mixing ratios. The rebuilding led to higher measurement precision and a reduction<br />

of sample volume and analysis time, both by a factor of two, and the data output is now homogenised<br />

for all sample components.<br />

Background The radiative forcing due to anthropogenic<br />

Greenhouse Gases released into the<br />

atmosphere accounts for approximately 1.5 W/m 2<br />

and is therefore the main contributor to global<br />

warming [Hansen et al. , n.d.]. Long term greenhouse<br />

gas records of high quality are important<br />

to determine the temporal change of these trace<br />

gases. Combined with isotopic data and regional<br />

or global models, the respective budgets can be<br />

investigated. In combination with 222 Rn data, local<br />

source and sink studies for greenhouse gases<br />

can be carried out.<br />

Funding This PhD work is funded by the EU<br />

projects TCOS - Siberia and CarboEurope-IP.<br />

Methods and results In order to couple the<br />

GCs by connecting the sample loops of both GCs<br />

in series, it was necessary to rebuild the sample<br />

inlet system. In addition, the capacity for<br />

flask sample measurements was doubled using a<br />

separate flask valve. It is now possible to measure<br />

twelve flasks within one sequence. To improve<br />

the CO reproducibility, a dedicated system<br />

of a backflush valve and resistances was developed<br />

and successfully installed. Along with the installation<br />

of these additional valves, the electronics<br />

devices were improved. The two former separate<br />

data acquisition systems were replaced by a new,<br />

state of the art, ChemStation Chromatography<br />

software. The rebuilding led to reduced sample<br />

volume and analysis time, which is particularly<br />

important for flask measurements. For the semicontinuous<br />

measurements in Heidelberg we gained<br />

a homogenised dataset. Since the rebuilding of<br />

the GC it is possible to determine H2 mixing ratios<br />

without further needs. The combined instrument<br />

now performs measurements of CO2, CH4,<br />

CO, N2O, SF6 and H2 every five minutes. Outside<br />

air is measured semi-continuously via two separate<br />

air intake lines, each of which is sampled at least<br />

once every 30 minutes. An example of the time<br />

series and the correlations between the different<br />

gas species is given in Figure 2.62.<br />

Figure 2.62: Half hourly mixing ratios of CO2,<br />

CO, CH4, N2O and H2 in Heidelberg. SW and<br />

SE mark the south-west and south-east air intake<br />

lines. Additionally 222 Rn daughter concentration<br />

and meteorological parameters are shown.<br />

Outlook/Future work It is now planned to<br />

apply the radon tracer method to the continuous<br />

H2 data to assess the sink strength of local soils.<br />

Furthermore, a detailed study on the vertical H2<br />

profile in soil air is planned to be performed by<br />

a diploma student. The long and extensive N2O<br />

records from worldwide monitoring stations will<br />

be analysed in a simple 2D model (Naegler, article<br />

2.7.2 this issue) to improve our understanding<br />

of the global N2O budget.


2.7. CARBON CYCLE GROUP 111<br />

2.7.4 Investigating CO2, CO and Fossil Fuel CO2 in Heidelberg<br />

Participating scientists Christoph Schönherr, Samuel Hammer, Bernd Kromer, Ulrike Gamnitzer,<br />

Ingeborg Levin<br />

Abstract In order to calibrate CO as a proxy for fossil fuel CO2 (CO2(fossil)), atmospheric CO<br />

mixing ratios in Heidelberg are being related to (CO2(fossil)) mixing ratios derived from 14 CO2 measurements.<br />

For extension of these investigations to sites without continuous gas chromatographic<br />

measurements, a device for integrated air sampling in a large bag was set up and tested.<br />

Figure 2.63: Integrated samples of CO2, CO, and 14 CO2 taken in Heidelberg for determination of the<br />

ratio CO/CO2(fossil). Blue symbols represent winter months, red symbols summer months; dotted<br />

lines are background mixing ratios. (a) Average CO2(total) mixing ratios during the respective<br />

sampling periods. (b) Same as (a), but for CO mixing ratios. (c) 14 CO2 depletions of the integrated<br />

samples, relative to the continental background. (d) CO2(fossil) mixing ratio as calculated from the<br />

CO2(total) mixing ratio and the 14 CO2 depletion. (e) CO/CO2(fossil) ratios for each sample, and<br />

the average ratio for all samples (solid black line).<br />

Background The global atmospheric mixing<br />

ratio of CO2 has been rising from about 280 ppm<br />

at the beginning of the 19th century to 378 ppm<br />

by the end of 2004, mainly due to the combustion<br />

of fossil fuels. This influences the Earth’s climate<br />

at present and very likely in the future. In order<br />

to estimate fluxes of CO2 into the atmosphere,<br />

it is necessary to separate the share originating<br />

from fossil fuel combustion. This can be achieved<br />

by radiocarbon ( 14 C) observations [Levin et al. ,<br />

2003], or by observation of another proxy, like carbon<br />

monoxide [Gamnitzer, 2003]. This proxy then<br />

has to be calibrated first by parallel 14 C measurements.<br />

Methods and results In a first part of my<br />

Diploma Thesis, the local gas chromatographic<br />

system (GC) was modernised for easier operation<br />

and more convenient data output. Second, using<br />

CO and 14 CO2 data from the years 2001 to<br />

2005, the CO/CO2(fossil) ratio for Heidelberg was<br />

studied. Samples taken during atmospheric inver-<br />

sion situations (events) with high local emissions<br />

signals yielded CO/CO2(fossil)=(1.06±0.33)%.<br />

Weekly and two-weekly integrated 14 CO2 samples<br />

influenced by a larger catchment area yielded a<br />

mean CO/CO2(fossil) ratio of (1.33 ± 0.29) %.<br />

Both methods can be used to assess fossil fuel<br />

CO2 for differently sized catchment areas. For<br />

determination of CO/CO2(fossil) at sites without<br />

continuous GC measurements, a device for integrated<br />

air sampling was set up and tested. This<br />

device is suited for non-biased sampling of CO2,<br />

CO, CH4, N2O, and SF6 during one week.<br />

Outlook/Future work The devices for integrated<br />

air sampling will now be set up in Paris and<br />

Krakow in the frame of the CarboEurope-IP to be<br />

run in parallel to integrated 14 CO2 measurements,<br />

in order to determine the regional CO/CO2(fossil)<br />

ratio with different emission characteristics.<br />

Main publication: Schönherr [2005]


112 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

References<br />

Gamnitzer, U. 2003. Bilanzierung der Kohlendioxidemissionen in der Region Heidelberg mit Hilfe<br />

atmosphärischer CO2-, 14 CO2- und CO-Messungen. Diploma thesis, University of Heidelberg.<br />

Hansen, J., Sato, M., Ruedy, R., Nazarenko, L., Lacis, A., Schmidt, G.A., Russell, G., Aleinov, I.,<br />

Bauer, M., Bauer, S., Bell, N., Cairns, B., Canuto, V., Chandler, M., Cheng, Y., Del Genio, A.,<br />

Faluvegi, G., Fleming, E., Friend, A., Hall, T., Jackman, C., Kelley, M., Kiang, N., Koch, D., Lean,<br />

J., Lerner, J., Lo, K., Menon, S., Miller, R., Minnis, P., Novakov, T., Oinas, V., Perlwitza, J.,<br />

Perlwitz, J., Rind, D., Romanou, A., Shindell, D., Stone, P., Sun, S., Tausnev, N., Thresher, D.,<br />

Wielicki, B., Wong, T., Yao, M., & Zhang, S. Efficacy of climate forcings), journal = JGR, year =<br />

2005, volume = 110, pages = doi:10.1029/2005JD005776,.<br />

Hesshaimer, V., Heimann, M., & Levin, I. 1994. Radiocarbon evidence for a smaller oceanic carbon<br />

dioxide sink than previously believed. Nature, 370, 201–203.<br />

Key, R. M., Kozyr, A., Sabine, C. L., Lee, K., Wanninkhof, R., Bullister, J. L., Feely, R. A., Millero,<br />

F. J., Mordy, C., & Peng, T.-H. 2004. A global ocean carbon climatology: Results from Global<br />

Data Analysis Project (GLODAP). Global Biogeoch. Cycl., 18(4), doi:10.1029/2004GB002247.<br />

Levin, I. 2004a. Greenhouse Gases Trends in Europe and at the German Antarctic Station. Invited<br />

talk, WMO WMO/GAW Expert Workshop on The Quality and Applications of European GAW<br />

Measurements. Tutzing, Germany.<br />

Levin, I. 2004b. Quantification of Exchange Rates in the Global Carbon Cycle by Radiocarbon Observations.<br />

Invited talk, Physical Colloquium. University of Groningen, The Netherlands.<br />

Levin, I. 2005a. Quantifying fossil fuel CO2 over Europe. Invited talk, Workshop on A Blueprint for<br />

a GHG monitoring system in Europe. Amsterdam, The Netherlands.<br />

Levin, I. 2005b. Recent Heidelberg Radiocarbon Observations in Atmospheric CO2. Invited talk,<br />

13th International WMO Experts Meeting on atmospheric CO2 and Related Tracer Measurement<br />

Techniques. Boulder (CO) USA.<br />

Levin, I., & Hesshaimer, V. 2000. Radiocarbon - a unique tracer of global carbon cycle dynamics.<br />

Radiocarbon, 42(1), 69–80.<br />

Levin, I., & Kromer, B. 2004. The tropospheric 14 CO2 level in mid-latitudes of the Northern Hemisphere<br />

(1959-2003). Radiocarbon, 46(3), 1 261–1 272.<br />

Levin, I., Glatzel-Mattheier, H., Marik, T., Cuntz, M., Schmidt, M., & Worthy, D.E. 1999. Verification<br />

of German methane emission inventories and their recent changes based on atmospheric<br />

observations. J. Geophys. Res., 104(D3), 3447–3456.<br />

Levin, I., Born, M., Cuntz, M., Langendörfer, U., Mantsch, S., Naegler, T., Schmidt, M., Varlagin,<br />

A., Verclas, S., & Wagenbach, D. 2002. Observations of atmospheric variability and soil exhalation<br />

rate of Radon-222 at a Russian forest site: Technical approach and deployment for boundary layer<br />

studies. Tellus, 54(5), 462–475.<br />

Levin, I., B. Kromer, M. Schmidt, & H. Sartorius. 2003. A novel approach for independent budgeting<br />

of fossil fuel CO2 over Europe by 14 CO2 observations. Geophysical Research Letters, 30(23), doi:<br />

10.1029/2003GL018477.<br />

Mayorga, E., Aufdenkampe, A. K., Masiello, C. A., Krusche, A. V., Hedges, J. I., Quay, P. D., Richey,<br />

J. E., & Brown, T. A. 2005. Young organic matter as a source of carbon dioxide outgassing from<br />

Amazonian rivers. Nature, 436, 538–541.<br />

Naegler, T. 2005 (June). Simulating Bomb Radiocarbon: Consequences for the Global Carbon Cycle.<br />

Ph.D. thesis, Insititut <strong>für</strong> <strong>Umweltphysik</strong>, University of Heidelberg, Heidelberg, Germany.<br />

Peacock, S. 2004. Debate over the ocean bomb radiocarbon sink: Closing the gap. Global Biogeoch.<br />

Cycl., 18, GB2022, doi:10.1029/2003GB002211.<br />

Röckmann, T., & Levin, I. 2005. High-precision determination of the changing isotopic composition<br />

of atmospheric N2O from 1990 to 2002. J. Geophys. Res. accepted.


2.7. CARBON CYCLE GROUP 113<br />

Schell, S. 2004. 222 Radon-Profil-Messungen in Süd- und Ostdeutschland, Anwendung der Radon-<br />

Tracer-Methode zur Berechnung von CO2- und CH4-Flüssen. Diplomarbeit, Insititut <strong>für</strong> <strong>Umweltphysik</strong>,<br />

University of Heidelberg. in German.<br />

Schönherr, C. 2005 (October). Investigating Carbon Dioxide, Carbon Monoxide and Fossil Fuel CO2<br />

in Heidelberg. Diplomarbeit, Insititut <strong>für</strong> <strong>Umweltphysik</strong>, University of Heidelberg.<br />

Spalding, K. L., Buchholz, B. A., Bergman, L.-E., Druid, H., & Frisén, J. 2005. Age written in teeth<br />

by nuclear tests. Nature, 437, 333–334.


Terrestrial Systems<br />

3.1 Soil Physics . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 117<br />

3.2 Ice and Climate . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 137<br />

115


3.1. SOIL PHYSICS 117<br />

Overview<br />

We study the whole range of physical processes in near-surface land systems, including the land<br />

cryosphere, at spatial scales ranging from sub-millimeter to hundreds of kilometers. These processes<br />

are relevant for a spectrum of hot environmental issues including water resources in arid and semi-arid<br />

regions, contamination of groundwater by agrochemicals and waste disposal site, as well as past and<br />

present climate changes. Current main research fields are<br />

1. movement of water and contaminants through soils into groundwater<br />

2. geophysical near-surface exploration and monitoring<br />

3. thermal and hydraulic dynamics of permafrost in a changing environment<br />

4. climate and environmental archives of glaciers and ice shields<br />

The group is organized in two major subgroups: “Soil Physics” covering research fields 1. . . 3 and “Ice<br />

and Climate” covering research field 4. An overview of their current research activities is given on<br />

pages 118ff and 137ff, respectively.<br />

Future Work<br />

Important perspectives for the next reporting period include<br />

1. extension of the Grenzhof test site to include electrical resistivity tomography (ERT) and additional<br />

ground-penetrating radar (GPR) measurements,<br />

2. investigation of frequency-dependent dielectric properties of soils as a basis for accurate measurements<br />

of soil water content at the field scale,<br />

3. setup of several monitoring stations on the Qinghai-Tibet plateau (China) to study the dynamics<br />

low-latitude permafrost and the impact of climatic warming,<br />

4. participation in the EPICA project (European Ice Core Drilling in Antarctica) through 10 Beinvestigations<br />

at the deep DML (Dronning Maud Land) ice core,<br />

5. attempts to date the basal layer of Alpine glaciers.<br />

More details are again given in the respective summaries.<br />

3.1 Soil Physics<br />

Members<br />

Dr. Andreas Bayer, PhD student<br />

Cand. Phys. Alexandra Herzog, diploma student<br />

Angelika Gassama, lab technician<br />

Dipl. Phys. Holger Gerhards, PhD student<br />

Dr. Olaf Ippisch, postdoctoral researcher<br />

Cand. Phys. Patrick Leidenberger, student<br />

Dr. Ing. Benedikt Oswald, senior scientist<br />

Dipl. Phys. Fereidoun Rezanezhad, PhD student<br />

Prof. Dr. Kurt Roth, group leader<br />

Dr. Anatja Samouëlian, postdoctoral researcher<br />

Cand. Phys. Klaus Schneider, diploma student<br />

Dr. Nadiya Smoljar, postdoctoral researcher<br />

Dipl. Phys. Carolin Ulbrich, PhD student<br />

PD Dr. Hans-Jörg Vogel, senior scientist<br />

Dr. Ute Wollschläger, senior scientist


118 CHAPTER 3. TERRESTRIAL SYSTEMS<br />

Background<br />

Transport of water, dissolved chemicals, and heat are intimately linked in soils and they are an important<br />

aspect of many environmental issues like quantity and quality of groundwater, irrigation and<br />

soil salinization, coupling of soil and atmosphere, and stability of permafrost soils. Major challenges<br />

are (i) the understanding of the physical basis of these highly nonlinear processes and (ii) the quantitative<br />

understanding of their manifestation at the scale of eventual interest. While the fundamental<br />

understanding typically refers to spatial scales of millimeters to meters, the scale of interest ranges<br />

from hundreds of meters, e.g., for optimized irrigation, to tens or hundreds of kilometers, e.g., for the<br />

impact of landuse changes on climate.<br />

Research Focus<br />

Our primary focus lies on understanding the physical basis of transport processes in soils, specifically<br />

the movement of water, of non-reactive solutes, and of thermal energy. We cover the range from<br />

detailed studies in the laboratory to monitoring at the field scale and from conceptual modeling to<br />

numerical simulation.<br />

A secondary focus is the development of novel approaches to (i) exploring subsurface structures<br />

and (ii) non-invasive measurements of state variables and material properties. Both are prerequisites<br />

for simulating large systems with time scales beyond reasonable experimentation and for monitoring<br />

transport processes.<br />

Project Clusters and Links<br />

Cluster A: Transport Processes<br />

At the lab scale, we study fundamentals of transport in porous media, currently water movement<br />

in coarse-textured media which may become unstable and lead to so-called flow fingers. These have<br />

been shown to be inconsistent with Richards’ equation which underlies most current models of water<br />

movement in soils. We study these instabilities in Hele-Shaw cells. Water saturation and dye<br />

distributions are determined by light transmission (project 3.1.3) which was previously calibrated by<br />

X-ray transmission (project 3.1.2). To improve the quality beyond that achieved with the white light<br />

transmission measurements, we look, with support from the image analysis group of Prof. Dr. Bernd<br />

Jähne, into near-infrared measurements within the absorption bands of water (project 3.1.4).<br />

Concurrent with our experimental studies, Sreejith Kuttanikkad in the parallel computing group<br />

of Prof. Dr. Peter Bastian at IWR develops a high-resolution solver for Stokes’ equation at the pore<br />

scale.<br />

At the small field scale, we investigate the impact of soil structures on water and solute movement.<br />

Of particular importance here are macropores – cracks and wormholes – which may lead to<br />

the bypassing of the biologically active layers. This has an impact on the availability of water for<br />

plants and on the decay of contaminants. An experimental study of so-called preferential flow was<br />

performed in cooperation with INRA at Orleans, Frankreich (Dr. Isabelle Cousin) (project 3.1.7) and<br />

successfully simulated numerically (project 3.1.8).<br />

At the large field scale, we operate test and monitoring sites at Grenzhof, Heidelberg, and near<br />

Ny-˚Alesund, Svalbard. Further sites are planned on the Qinghai-Tibet plateau, China.<br />

The Grenzhof site, located a few kilometers from Heidelberg, is dedicated to exploring transport<br />

processes in natural soils, eventually also the coupling between soil and atmosphere, and to developing<br />

and testing new measuring methods and instruments. Its primary advantages are easy access and<br />

vicinity to the institute.<br />

The site is 20 m × 10 m in size. It is equipped with an automated weather station (air temperature,<br />

humidity, and pressure, wind speed and direction, precipitation, radiation components), a profile of<br />

ground temperature sensors down to 1.6 m, and two profiles of time-domain reflectometry (TDR)<br />

probes for measuring liquid water content down to 1.4 m.<br />

During the installation of the ground instruments, large soil cores where extracted whose hydraulic<br />

properties are measured in the lab as described below on “Inverse Determination of Soil Hydraulic<br />

Properties”.<br />

Weekly measurements with ground-penetrating radar (GPR) yield novel information on the dynamics<br />

of soil water content at the field scale which is compared with the point measurements provided<br />

by TDR (project 3.1.9).


3.1. SOIL PHYSICS 119<br />

In November 2004, a tracer experiment was started and monitored with soil coring, TDR, GPR,<br />

and electrical tomography, the later by our cooperation partners from the Dresdner Grundwasserforschungszentrum<br />

(DGFZ). The experiment was sampled, in the classical destructive way, in April<br />

2005 (project 3.1.10).<br />

Funding for this site is provided primarily by DFG through a joint project with DGFZ (Dr. Frank<br />

Börner), and TU Freiberg (Prof. Dr. Bernhard Forkmann) and supplementary by IUP.<br />

Future The Grenzhof site is currently expanded to 200 m × 10 m to allow for large-scale<br />

measurements, primarily with GPR. In addition, we plan to install our own and permanent electrical<br />

resistivity tomography (ERT) equipment early 2006. This will be used to monitor a new tracer<br />

experiment with high temporal resolution. In addition, we want to explore the feasibility of monitoring<br />

the dynamics of soil water content with ERT.<br />

The two sites near Ny-˚Alesund, Svalbard are aimed at understanding the thermal and hydraulic<br />

dynamics of arctic permafrost. They are equipped with two-dimensional arrays of temperature- and<br />

TDR-sensors, some 30 of each at both sites, and Bayelva in addition has a weather station as already<br />

described for the Grenzhof site. The NP site is very near to the corresponding station at Ny-˚Alesund.<br />

Both sites were installed and are operated in cooperation with the Alfred Wegener <strong>Institut</strong>e (AWI),<br />

Potsdam (Dr. Julia Boike). They deliver data since September 1998, with some interruptions due to<br />

damage by reindeer.<br />

The original installation and operation of the sites was funded by DFG, the corresponding project<br />

was completed in 2001. The current operation and maintenance is covered by AWI and the stream of<br />

data is collected and processed at IUP. The original goal of understanding the thermal and hydraulic<br />

dynamics was achieved. The two stations are now oriented towards monitoring the response to climatic<br />

changes.<br />

Future We plan to set up four monitoring stations similar to those installed on Svalbard on the<br />

Qinghai-Tibet plateau, China. They will be aimed at understanding the dynamics of low-latitude<br />

permafrost, which is characteristically different from arctic permafrost due to the different radiation<br />

regime. Besides the local dynamics, we also want to study the impact of the current climatic warming<br />

on the decay of the permafrost. The major tool for this second aspect will be GPR explorations<br />

(project 3.1.13) on long lines in the vicinity of the stations.<br />

This project is funded by DFG and Chinese Academy of Sciences (CAS). Cooperation partners<br />

are Dr. Yu Qihao and Dr. Jin Huijun of the Cold and Arid Regions Environmental and Engineering<br />

Research <strong>Institut</strong>e (CAREERI) and CAS, Lanzhou.<br />

Cluster B: Geophysical Exploration and Monitoring<br />

Geophysical instruments are increasingly used for near-surface investigations of soils, permafrost,<br />

and glaciers and for the non-destructive semi-quantitative monitoring of transport processes. Our<br />

interest is currently focused on electromagnetic waves in the frequency range between 50 MHz and<br />

2 GHz which allow the mapping and monitoring of dielectric structures. These in turn are strongly<br />

influenced by the volume fraction of liquid water which has a dielectric number εw ≈ 80 that is<br />

about an order of magnitude larger than that of other relevant constituents. Since soil and geologic<br />

formations typically differ in texture, and thus in equilibrium water content, the dielectric structure<br />

of the subsurface typically also reveals its architecture. We employ two classes of instruments, timedomain<br />

reflectometry (TDR) which operates with guided waves and ground-penetrating radar (GPR)<br />

which is based on free waves. Our primary aim here is to develop a hierarchy of instruments and<br />

methods to measure the volumetric water content at scales from a few centimeters to a few kilometers.<br />

TDR has been developed and used for a long time to measure average volumetric water content<br />

within the sampling volume of the probe, typically a cylinder some 50 mm in diameter and 200 mm<br />

long [Roth et al. , 1990]. A new development is the use of much longer probes in conjunction with<br />

the inversion of the time-domain signal to obtain the spatial variation of the dielectric number along<br />

the probe instead of its average (project 3.1.11). Such an instrument is particularly attractive near<br />

the soil surface since the water content there changes very rapidly both in space and in time.<br />

GPR has the advantage that no installations are required – the antennas are just pulled across<br />

the soil surface – and thus facilitates measurements on long transects with lengths of hundreds of<br />

meters to a few kilometers. Two groups of waves may be distinguished in a typical GPR application,<br />

the ground wave which propagates as an evanescent wave along the soil-air interface, and the reflected<br />

waves that originate at dielectric discontinuities. Both yield valuable information on the water content<br />

and, to a limited degree, on solute distributions. Besides the heuristic analysis of GPR and comparison<br />

with TDR (project 3.1.9), we investigate the inversion of the signals. As a first step, semi-analytical<br />

(project 3.1.13) and numerical (project 3.1.12) forward solutions are developed and their performance<br />

is explored. The associated calculations are rather time-consuming and run on our Linux-cluster.


120 CHAPTER 3. TERRESTRIAL SYSTEMS<br />

Future Activities at the Grenzhof site will be expanded along two lines: (i) We will explore the<br />

potential of GPR-trains (multiple coupled antennas) to yield concurrent information on the depth of<br />

reflectors and on soil water content. (ii) We want to perform a comparative study of different methods<br />

for measuring near-surface soil water content. Methods used will be soil sampling, vertical TDR, GPR<br />

groundwave, and GPR reflection. This study is a prerequisite for the accurate interpretation of data<br />

obtained satellite instruments (synthetic apperture radar (SAR) and radiometry as it will be available<br />

from SMOS after 2007).<br />

Cluster C: Effective Material Properties<br />

Soils contain relevant structures on many scales, from a few micrometers all the way up to the landscape.<br />

Effective material properties which summarize the impact of physical processes below some<br />

particular scale are a convenient approach to limit the complexity of models and simulations at scales<br />

of practical interest. These effective properties are of fundamental interest in their own right – under<br />

what circumstances do they exist and how can they be defined objectively? – but the immediate<br />

interest is typically to get hands on optimal estimates of their functional form and the corresponding<br />

parameters.<br />

Hydraulic properties, the soil water characteristic θ(ψm) and the hydraulic conductivity function<br />

K(θ) are prerequisites for the numerical simulation of water movement through soils. We employ<br />

the traditional multi-step outflow (MSO) method to (i) routinely estimate these functions and (ii) investigate<br />

effective properties of heterogeneous media (projects 3.1.2 and 3.1.1). In this method, an<br />

initially completely saturated soil column is drained by reducing the pressure at its lower end in a<br />

number of discrete steps. Pressure and outflow are recorded and inverted to obtain highly nonlinear<br />

functions θ(ψm) and K(θ).<br />

The MSO method is limited to rather high potentials – pressure cannot be reduced below the<br />

vapor pressure – and does not yield useful information for fine-textured soils. To obtain a much more<br />

extended range, we develop a new method where water is evaporated from the sample’s surface. This<br />

allows very low potentials by simply reducing the humidity of the incoming air. The vapor flux is<br />

measured spectroscopically (project 3.1.5) and again inverted numerically with a code developed by<br />

Olaf Ippisch (IWR and IUP).<br />

A crucial aspect of the inversion procedure, both for the traditional MSO and for the evaporation<br />

experiment, is the parameterization of θ(ψm) and K(θ). The current approaches are almost universally<br />

based on the Mualem-van Genuchten parameterization. In cooperation with IWR (Prof. Dr. Hans-<br />

Georg Bock) a free parameterization based on monotone spline functions is developed (project 3.1.6)<br />

and implemented in the inversion code by Olaf Ippisch (IWR and IUP).<br />

Funding for the projects on effective hydraulic properties is provided in part by BMBF (“Sickerwasserprognose”)<br />

and by DFG.<br />

Dielectric properties, the soil’s complex dielectric number ε, depend strongly on liquid water<br />

content and moderately on temperature, frequency, solute concentration, and soil composition. They<br />

provide the link between the electromagnetic measurements and the quantities of interest, primarily<br />

soil water content and secondarily solute concentration.<br />

The traditional approaches consists in identifying a regression relation between the quantities of<br />

interest [Topp et al. , 1980] or in postulating a dielectric mixing model εc = f({θi, εi}), where εc<br />

the measured (composite) dielectric number and {θi, εi} are volume fraction and (known) dielectric<br />

number of the set of constituents i [Roth et al. , 1990]. Both approaches are used for the direct analysis<br />

of the type of broadband signals used in TDR and GPR. In some earlier work in cooperation with<br />

Prof. Dr. Markus Flury, Washington State University, Pullman, USA, and Dr. Marco Bittelli, now<br />

at University of Bologna, Italy, we showed that narrow-band measurements (dielectric spectroscopy)<br />

yield more information on different soil constituents and in particular allow the distinction between<br />

liquid and frozen water [Bittelli et al. , 2004].<br />

For the next step, we developed a large coaxial cell for dielectric measurements of geologic samples<br />

for frequencies 0.3. . . 3’000 MHz using a network analyzer together with the required robust inversion<br />

code [Oswald et al. , 2006]. A first series of calibration runs with different liquids and partly saturated<br />

sands have been completed successfully.<br />

Future Preliminary studies of soil samples from the Grenzhof site revealed a rather strong<br />

frequency-dependence of dielectric properties. This has a strong impact on water content measurements<br />

with electromagnetic methods and requires further detailed investigation.


3.1. SOIL PHYSICS 121<br />

Major Achievements<br />

1. Demonstration that water content profiles can be obtained from GPR measurements and their<br />

accuracy rivals that of TDR (project 3.1.9).<br />

2. Modeling and numerical simulation of solute transport through a soil with macropores (projects 3.1.7<br />

and 3.1.8).<br />

Publications<br />

Peer Reviewed Publications<br />

1. Oswald et al. [2006]<br />

2. Roth et al. [2005]<br />

3. Stöhr & Roth [2005]<br />

4. Bayer et al. [2005]<br />

5. Yu et al. [2005]<br />

6. Vogel et al. [2005a]<br />

7. Vogel et al. [2005d]<br />

8. Vogel et al. [2005e]<br />

9. Wollschläger & Roth [2005]<br />

10. Braun et al. [2005]<br />

PhD Theses<br />

1. Bayer [2005]<br />

Diploma Theses<br />

1. Herzog [2005]<br />

2. Ulbrich [2005]<br />

3. Herzog [2005]<br />

Invited Talks<br />

1. Vogel [2005b]<br />

2. Vogel et al. [2005c]<br />

3. Vogel [2005c]<br />

4. Vogel [2005a]<br />

5. Oswald & Roth [2005c]<br />

6. Roth & Wollschläger [2005]<br />

7. Roth [2005a]<br />

8. Roth [2005b]<br />

9. Roth [2005c]


122 CHAPTER 3. TERRESTRIAL SYSTEMS<br />

3.1.1 Estimation of effective hydraulic parameters for heterogeneous porous<br />

media<br />

Participating scientist Anatja Samouëlian, Hans Jörg Vogel<br />

Abstract Through numerical simulations and experimentations, the influence of small scale heterogeneity<br />

on large scale hydraulic properties of soil was investigated. The effective water capacity<br />

is directly related to the probability densities function for the texture of the composites, while the<br />

hydraulic conductivity additionally depends on its topology.<br />

Figure 3.1: a) Three types of heterogenous media where the grey value corresponds to characteristic length<br />

of subscale porous medium, b) effective water retention curve for the three fields (predicted in yellow, grey<br />

area represents the small scale heterogeneity), c) the regression between hydraulic conductivity exponent and<br />

topological variable.<br />

Background Soil hydraulic properties can be<br />

estimated using multi-step-outflow experiments<br />

(MSO) in combination with inverse modeling.<br />

One assumption implied, is that the sample is<br />

large enough to contain all microscopic heterogeneities<br />

in the sense of a representative elementary<br />

volume (REV). Hence, the measured properties<br />

are considered as an ‘effective‘ description.<br />

However these ideal conditions are rarely met,<br />

since soil is typically heterogeneous at various hierarchical<br />

scales.<br />

The question for this project is: Given the<br />

measured effective properties together with the<br />

entire 3D structure of the composites (measured<br />

by X-ray tomography) is it possible to estimate<br />

the properties of each single component?<br />

As a first step we investigate the functional<br />

relation between structural features and the effective<br />

hydraulic properties through numerical simulations<br />

using well defined random fields.<br />

Funding DFG project 2004-2005 VO 566/5-1<br />

Methods and results Numerical experiments<br />

were performed on heterogeneous media: (i) a<br />

standard Gaussian field, (ii) a field where the fine<br />

textured material is highly connected and (iii) a<br />

field where the coarse textured material is connected<br />

(fig.1a). The hydraulic properties are described<br />

assuming Miller-similarity. Their topol-<br />

ogy, quantified by the Euler number is different,<br />

however, the first two moments, mean and covariance,<br />

are identical for the three random fields.<br />

The simulated water retention curves for the<br />

three fields are identical and can be directly calculated<br />

from the histogram of the components by<br />

θeff (ψ) = �<br />

i [ωiθi(ψ)] for i materials and their<br />

probability density ωi (fig. 1b).<br />

Concerning the hydraulic conductivity, the<br />

topology of the structure is a key to predict the<br />

effective behaviour. It can be approached by<br />

Keff (ψ) q = �<br />

i [ωiKi(ψ) q ] with q an exponent<br />

related to the topology of the conductivity field.<br />

The first results indicate a polynomial regression<br />

between the calculated exponent q and the measured<br />

topology (fig. 1c).<br />

Outlook/Future work The quantitative link<br />

between structural quantities and effective hydraulic<br />

properties, both accessible through direct<br />

measurement, will greatly facilitate the estimation<br />

of the subscale parameter field. Based on this information<br />

the phenomenology of water flow and<br />

solute transport can be predicted for natural heterogeneous<br />

soil.<br />

Main publication Samouëlian et al., Averaging<br />

of hydraulic properties in heterogeneous<br />

porous media (to be submited)


3.1. SOIL PHYSICS 123<br />

3.1.2 X-ray attenuation techniques to study the dynamics of water in<br />

porous media<br />

Participating scientist Andreas Bayer, Hans-Jörg Vogel, Kurt Roth<br />

Abstract X-ray attenuation was used as non-invasive method to monitore the distribution of water<br />

in samples of porous media during a multistep-outflow experiment. Differences between the data and<br />

a numerical inversion that aimed at effective material properties reveal the impact of soil structures<br />

at different scales.<br />

0 1<br />

40 50 60 70<br />

time [h]<br />

0<br />

−20<br />

−15<br />

cumulative outflow [cm]<br />

1<br />

−10<br />

2<br />

−5<br />

boundary condition [cmWC]<br />

0<br />

3<br />

−0.5<br />

5<br />

diff. [cm]<br />

0<br />

0.5<br />

sample height [cm]<br />

10<br />

8<br />

6<br />

4<br />

2<br />

0<br />

0 0.1 0.2 0.3 0.4<br />

water content [-]<br />

sample height [cm]<br />

10<br />

8<br />

6<br />

4<br />

2<br />

0<br />

0 0.1 0.2 0.3 0.4<br />

water content [-]<br />

Figure 3.2: Left: Measured cumulative outflow (black circles) and results of inverse modeling (black<br />

lines). Red lines shows predicted outflow assuming layered material model. Green symbols and lines<br />

represent outflow obtained for layered material model turned upside down with effective properties<br />

again obtained by inversion. Center: Measured (symbols) and simulated (solid lines) vertical water<br />

distribution at hydrostatic equlibrium for different outflow steps assuming uniform sample. Right:<br />

Same as the center but simulation based on layered model.<br />

Background The description of the dynamics<br />

of water in soil leads to the introduction of effective<br />

properties. For large scales, order of 1 m and<br />

beyond, soils and aquifers have a distinctive heterogeneous<br />

architecture of soil layers and sedimentary<br />

units, respectively. These units are presumed<br />

to be uniform and are represented by a set of effective<br />

material properties which in turn are measured<br />

in the lab, typically by multistep-outflow<br />

experiments. This approach does not explicitly<br />

address the well-documented multiscale heterogeneity<br />

of natural porous media which extends to<br />

scales much smaller than 1 m. In this project, the<br />

impact of heterogeneity on the typical analysis of<br />

a multistep-outflow experiment is explored.<br />

Funding BMBF (“Sickerwasserprognose”)<br />

Project 02WP0261<br />

Methods and results A non-invasive method<br />

to obtain information about the assumed sample<br />

structure is X-ray attenuation and tomography.<br />

It was combined with a multistep-outflow setup<br />

to assess the sample’s structure and to monitor<br />

the distribution of water during the experiment.<br />

Vertical water content profiles extraxted from<br />

X-ray attenuation data were compared with<br />

profiles simulated based on Richards equation<br />

(fig. 3.2, middle). The simulation used hydraulic<br />

parameters estimated from the inversion of measured<br />

outflow data (fig. 3.2, left). The dramatic<br />

differences between measured and predicted profiles<br />

are typically not observed because the corresponding<br />

instrumentation is not available. The<br />

origin of the difference is a weak layering produced<br />

during sample preparation and is representative<br />

for a rather uniform natural porous medium. Inversion<br />

of the data did not hint at this complication:<br />

the fit represents the outflow data very well.<br />

To investigate the issue, we set up a layered<br />

model based on the X-ray attenuation profiles<br />

and hydraulic parameters obtained from forward<br />

simulations. The modeled outflow fits both, the<br />

measured outflow and the vertical water content<br />

distribution, reasonably well. Notice that there<br />

was no inversion used in this approach. This illuminates<br />

the difficulties to estimate effective hydraulic<br />

properties in a “blind experiment” where<br />

the internal structure is not represented. We<br />

demonstrated that X-ray measurements provide<br />

the crucial additional information required for<br />

a faithful model of the hydraulic behavior of a<br />

porous material, at least for the simple case studied<br />

here.<br />

Main publication Bayer, A., PhD thesis 2005;<br />

Bayer et al. [2004]; Bayer et al. [2005]


124 CHAPTER 3. TERRESTRIAL SYSTEMS<br />

3.1.3 Fingered Flow Through Initially Dry Porous Hele-Shaw cell<br />

Participating scientist Fereidoun Rezanezhad, Hans-Jörg Vogel, Kurt Roth<br />

Abstract Fingered flow is an instability that occurs during infiltration into dry, coarse-textured,<br />

and uniform porous media. We study the dynamics of such fingers in porous Hele-Shaw cells with<br />

dimensions 1.6 × 0.6 × 0.003 [m]. High-resolution measurements of the water saturation are obtained<br />

from light transmission images that have been calibrated by X-ray transmission.<br />

Background Unstable flow of water during infiltration<br />

into unsaturated porous media belongs<br />

to the class of preferential flow. It has been studied<br />

for many years and we have a quite complete<br />

description of the general phenomena. Glass and<br />

Nicholl (1996) reviewed the classical understanding<br />

and DiCarlo (2004) summarizes the newer<br />

developments which focus on the nature of the<br />

saturation overshoot in the finger tip. Fingered<br />

flow is important for some practical issues, e.g.,<br />

for rapid contaminant transport with irrigation in<br />

many arid regions. However, it also illuminates<br />

our very understanding of the physics of multiphase<br />

flow in porous media. Indeed, the current<br />

theory – Richards equation – cannot explain the<br />

existence of such fingers.<br />

Funding DFG RO 1080/9-1&2<br />

Methods and Results The key to understanding<br />

fingered flow are rapid high-resolution measurements<br />

of the water saturation. To facilitate<br />

this, we work with Hele-Shaw cells – two parallel<br />

glass plates separated by a few millimeters –<br />

that are filled with sand. Light transmission is<br />

the used as a proxy for water saturation. A simple<br />

digital camera then yields the required rapid measurements.<br />

Since the relation between transmission<br />

and saturation is nonlinear, it is calibrated<br />

with X-ray transmission which is accurate but too<br />

slow and also too expensive for routine measurements.<br />

In our experiments, fingers are initiated<br />

at the transition from a fine-textured layer, where<br />

the flow is very uniform, to a coarse-textured<br />

Figure 3.3: Experimental setup for X-ray and<br />

light transmission measurements. The front<br />

view shows the highly localized flow paths that<br />

originate from the flow instability in the uniform<br />

part of the medium.<br />

layer. They eventually disappear into the simulated<br />

groundwater at the lower end of the cell. At<br />

different stages, a dye tracer is added to the flow in<br />

order to study the flow field behind the finger tip.<br />

Finally, pressure sensors are installed to monitor<br />

the potential energy of the water.<br />

First, a number of experimental findings of<br />

other groups were reproduced. These are in particular<br />

(i) the maximum saturation that occurs in<br />

the finger tip, (ii) the stability of the resulting flow<br />

channel on short time scales and its diffusive decay<br />

on very long time scales, and (iii) the existence of a<br />

mobile core and an immobile fringe. Some newer<br />

findings include (i) the demonstration that flow<br />

channels are destroyed when they encounter heterogeneous<br />

layers, (ii) the detection of pressure<br />

drops in the overlaying fine-textured layer upon<br />

initialization of a new finger, and (iii) the detection<br />

of correlated intermittency between different<br />

fingers.<br />

Outlook/Future Work The future work will<br />

concentrate on the theoretical understanding of<br />

the experiments. This necessitates a still higher<br />

spatial resolution, however, which in turn requires<br />

a more detailed representation of the light transmission<br />

through the porous medium. Measurements<br />

of the point spread function in the nearinfrared<br />

as well as in the visible region are under<br />

way (project 3.1.4). On another route, a microscope<br />

was installed that allows the resolution of<br />

the pore space and the detailed observation of the<br />

water phase during the passage of a finger tip.


3.1. SOIL PHYSICS 125<br />

3.1.4 Near Infrared Imaging Spectroscopy of Water States in Porous Silicate<br />

Media<br />

Participating scientist Nadiya Smolyar, Kurt Roth, Bernd Jähne<br />

Abstract We have examined capillary and adsorbed water in porous silicates (quartz sand, clay,<br />

silica gel) by using of Near Infrared Image Spectroscopy, NIRIS. The interaction of water with the<br />

porous media, the spatial distribution of water content, and the physics of different water states, as<br />

well as their transformation will be studied.<br />

Figure 3.4: Spectral transmission images of capillary water in sand at different times t1(a) < t2(b),<br />

showing the distribution of water content and state.<br />

Background NIRIS examinations are important<br />

for understanding the molecular mechanisms<br />

of water interacting with porous silicate media.<br />

Even today, the role water plays in the quality of<br />

soils and in further environmental effects is not<br />

unterstood in many aspects.<br />

Methods and results Capillary and adsorbed<br />

water is examined spectrally in both dry and<br />

saturated silica specimens. The frequency spectra<br />

are measured in near infrared (ν = 3300 −<br />

11000cm −1 ; λ = 700 − 3000nm) with a UV-NIR<br />

spectrometer Scan 500 (Varian,USA).<br />

The frequency values, the characteristic intensities,<br />

and appearance of new spectral bands of water<br />

in SiO2 media yield numerous data as elasticity<br />

constants, bond geometries, and adsorption<br />

mechanisms. The analysis of OH vibration<br />

modi permits the determination of water content<br />

along with changes of water states in the silicate<br />

medium. We have found that the water content<br />

can be determined best by using the intensive<br />

bands 2νOH and νOH + ν2, and the water state<br />

according to the bands 3νOH and 2νOH+ν2.<br />

A new innovative NIRIS method has been developed<br />

for investigations on the spectral optical<br />

qualities of water in porous specimens with spatial<br />

resolution. To this end, an imaging multispectral<br />

32-channel CCD spectrometer has been set up.<br />

The corresponding CCD camera takes sequences<br />

of spectral images at certain wavelengths using<br />

band pass filters. The images are by spectral digital<br />

image processing analyzed.<br />

Outlook/Future work The NIRIS concept<br />

permits the determination of molecular interaction<br />

forces of water on solid boundaries and micro<br />

pores together with the physics of water states and<br />

measuring the water distribution on porous silicates.<br />

The results will aid in gaining deeper understanding<br />

of the thermodynamical, structural,<br />

and dynamic characteristics of water in silicate<br />

media. We are planning the following investigations<br />

of water in porous silicate media:<br />

-Relation of multiple light scattering for determination<br />

of true values of water absorption; -<br />

Investigation of different water states, their spatial<br />

distribution and concentration; -Investigation<br />

of the stationary and dynamic water regimes; -<br />

Spectral analysis of the influence of physical factors<br />

on the interaction of water and medium; -<br />

Investigation of multi-phase systems with various<br />

kinds of intermolecular interaction.<br />

Main publication Smolyar N., M. Korniyenko<br />

and K. Roth (2005) Near Infrared imaging spectroscopy:<br />

A new tool for studying water states<br />

and movement in porous media, ’Geophysical Research<br />

Abstracts’, EGU05-A-07910.<br />

Smolyar N. (2003) Bildgebende Spektroskopie<br />

an Pflanzenblättern. Dissertation, <strong>Universität</strong><br />

Heidelberg, Interdisziplinäres Zentrum <strong>für</strong> Wissenschaftliches<br />

Rechnen (IWR), 195 S.<br />

Garbe C., N. Smolyar, M. Korniyenko and<br />

U. Schurr (2003) Water relations in plant leaves,<br />

Springer Verlag. Lecture Notes in Computer Science,<br />

LNCS 19: 377-401.


126 CHAPTER 3. TERRESTRIAL SYSTEMS<br />

3.1.5 Evaporation Experiment to determine Soil Hydraulic Properties<br />

Participating scientist Klaus Schneider, Kurt Roth<br />

Abstract A new enhanced evaporation experiment has been set up to measure soil hydraulic properties.<br />

The water flux and the potential at the upper boundary are measured precisely using infrared<br />

absorption. Hydraulic properties are determined by inverse numeric modelling, thereby explicitely<br />

simulating the diffusive water transport at the surface.<br />

air conditioning<br />

pressure sensor<br />

capillary<br />

vacuum pump<br />

IR gas analyser evaporation chamber<br />

Cell A<br />

Cell B<br />

temperature sensor<br />

TDR<br />

soil<br />

pressure sensor<br />

Figure 3.5: Schematic of the experimental setup of the evaporation experiment. IR spectroscopy<br />

allows precise potential and water flux measurement at the upper boundary.<br />

Background An important issue in soil physics<br />

is the determination of the hydraulic parameters<br />

of soils. If the soil water characteristic θ(ψm)<br />

and the conductivity function K(θ) of a soil are<br />

known, its hydraulic dynamics can be simulated<br />

using Richard’s equation.<br />

Several methods exist to determine the hydraulic<br />

properties in the laboratory. As these<br />

are highly non-linear functions, numeric simulation<br />

and inverse modelling provide a flexible tool<br />

to determine them with reasonable accuracy.<br />

It is generally desireable to know the hydraulic<br />

properties in a wide range of potential and water<br />

content. However, methods are always limited to<br />

a certain range, and hydraulic properties normally<br />

are not valid outside the measured range.<br />

For the wet range with potentials up to about<br />

ψm = −1.8 · 10 4 J/m 3 (corresponding to a water<br />

column of −1.8 m), the multistep-outflow (MSO)<br />

method is already well established. To obtain<br />

valid hydraulic properties also for the dry range,<br />

an evaporation method is developed. It will be<br />

used after an MSO experiment. Ideally this allows<br />

to obtain the desired functions in one run.<br />

Problems of traditional experiments The<br />

traditional setup for evaporation method uses a<br />

balance to measure the cumulative outflow at<br />

the upper boundary and tensiometers at different<br />

heights to measure potentials. The soil is initally<br />

saturated and free evaporation is allowed to start<br />

(Wendroth et al 1993).<br />

The major drawbacks of this setup are:<br />

• With free evaporation, the boundary condition<br />

at the upper boundary is not well defined.<br />

• The potential at the upper boundary is not<br />

known.<br />

• The range is limited, because tensiometers only<br />

work until ψm ≈ −5 · 10 4 J/m 3<br />

• Weighting to determine the flow at the upper<br />

boundary is problematic in the dry region, because<br />

water content change is very small.<br />

Methods and results To avoid these problems,<br />

a new design of experimental setup was<br />

used, which is shown schematically in figure 3.5. A<br />

gas-tight chamber is placed on top of the soil sample,<br />

and air with defined water vapour contents is<br />

flowing through the chamber. As the potential<br />

of the air is determined by its relative humidity,<br />

the upper boundary condition can be controlled<br />

precisely. The water vapour content of the air<br />

is measured before and after the chamber by infrared<br />

absorption. This allows very precise flux<br />

and potential measurements, while at the same<br />

time abandoning the usage of tensiometers and<br />

balance. The method is thus applicable even in<br />

the very dry region.<br />

Additionally, numerical simulation allows explicit<br />

modelling of the diffusive water transport in<br />

the boundary layer, enhancing the results and the<br />

insight into the physical processes.<br />

Outlook / Future work The setup is currently<br />

in its test phase, but first data look promising.<br />

The numerical inversion must still be completed.<br />

Main publication Diplomarbeit planned for<br />

December 2005.<br />

evaporation


3.1. SOIL PHYSICS 127<br />

3.1.6 Free Parameterisation of Soil Hydraulic Properties<br />

Participating scientists A. Herzog, O. Ippisch, S. Körkel, E. Kostina, K. Roth, J. Schlöder<br />

Abstract In order to cope with multi-modal soil water characteristic and permeability functions a<br />

local parameterisation based on piecewise cubic Hermite polynomials is used.<br />

volumetric water content<br />

Mualem−van Genuchten parametrisation<br />

original bimodal soil water characteristic<br />

applied suction pressure [Pa]<br />

Figure 3.6: Sketch of a bimodal soil water characteristic together with Mualem-van Genuchten<br />

parametrisation.<br />

Background It is expected that soils with<br />

multi-modal hydraulic functions (i.e. soil water<br />

characteristic and permeability function) exist in<br />

nature. As the hydraulic functions are mainly<br />

obtained by inverse modelling and not by direct<br />

measurement a parameterisation is needed that is<br />

flexible enough to handle all cases. Specifically,<br />

the widely-used Mualem-van Genuchten parameterisation<br />

is too restrictive to describe the actual<br />

functions satisfactorily. With these problem specifications<br />

water transport through these materials<br />

cannot be described accurately.<br />

Different approaches have been proposed in<br />

the last ten years. Among those are a piecewise<br />

linear parameterisation introduced by Chardaire-<br />

Riviere et al. (1990) and a piecewise cubic Hermite<br />

parameterisation introduced by Knabner et<br />

al. (Aug. 2004).<br />

Also in this thesis piecewise cubic Hermite<br />

parametrisation is investigated in the context<br />

of a simulation programme for water transport<br />

through soil.<br />

Funding Diplomarbeit<br />

Methods and results In this thesis a simulation<br />

programme for water transport is used (Ippisch,<br />

2001). The deviation between model response<br />

and measured values is to be minimised.<br />

The hydraulic functions are part of the model response<br />

in parameterised form.<br />

The simulation programme includes a minimisation<br />

routine for solving for the unknown soil parameters.<br />

The hydraulic functions are parameterised<br />

by piecewise cubic Hermite polynomials.<br />

This parameterisation guarantees C 1 continuity.<br />

Mainly, two different modifications of the parameterisation<br />

of Knabner et al. are tested:<br />

1. A piecewise cubic Hermite parameterisation<br />

using approximated derivatives according to the<br />

formulas of Butland and Brodlie. This parameterisation<br />

is local, in contrast to the one of Knabner<br />

et al..<br />

2. The derivatives themselves are not approximated<br />

but also treated as parameters. parameterisation.<br />

This approach leads to the best results<br />

when started with rather good initial values,<br />

which are gained by solving the inverse problem<br />

with the parameterisation described in (1). However,<br />

this parameterisation is again non-local.<br />

For bimodal hydraulic functions it could be<br />

demonstrated that the used piecewise Hermite parameterisation<br />

is much more convenient than the<br />

Mualem-van Genuchten parameterisation.<br />

With the derivatives as additional parameters<br />

a new problem arises: Some plateaus appeare in<br />

the hydraulic functions where, physically, they are<br />

not expected. They might be artefacts of the revision<br />

of derivatives.<br />

Outlook/Future work In order to avoid these<br />

plateaus it is intended to create a parameterisation<br />

that has still the C 1 continuity but resembles<br />

more closely a piecewise linear interpolation. This<br />

can be achieved by a much more restrictive selection<br />

of the allowed derivatives.<br />

Main publication Herzog, Alexandra, Diplomarbeit,<br />

Interdisziplinäres Zentrum <strong>für</strong> wissenschaftliches<br />

Rechnen/<strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>,<br />

<strong>Universität</strong> Heidelberg, 2005


128 CHAPTER 3. TERRESTRIAL SYSTEMS<br />

3.1.7 Modelling water flow and solute transport in heterogeneous soil<br />

Participating scientist Hans-Jörg Vogel, Isabelle Cousin, Olaf Ippisch<br />

Abstract Flow and transport in soil is governed by the heterogeneous structure of the material.<br />

In this project we consider the structure using different concepts: direct measurement, statistical<br />

description and modelling structure formation. Based on this rough representation we estimate water<br />

flow and solute transport. This is possible because the processes are dissipative.<br />

A<br />

B<br />

C<br />

Figure 3.7: Soil profile with three horizons (A, B, C) and the distribution of a dye tracer (left),<br />

modelled structural components: correlated random fields and earthworm burrows (middle), and<br />

predicted tracer distribution (right).<br />

Background The quantitative understanding<br />

of flow and transport in soil is hampered by<br />

the heterogeneous structure of the material which<br />

cannot be represented by a meaningful average<br />

value. This is typically true at any spatial scale.<br />

To predict the movement of chemicals between the<br />

soil surface and groundwater this structure has to<br />

be represented adequately.<br />

Funding Deutscher Akademische Auslandsdienst<br />

(DAAD, PROCOPE project).<br />

Methods and results In this project we used<br />

a dye tracer in a field experiment on arable soil to<br />

visualize the tracer distribution after a cumulative<br />

infiltration of 50 mm of water. To model this experiment,<br />

the structure of the soil was represented<br />

using three different approaches: i) direct measurement<br />

of the soil horizons in the field (A,B,and<br />

C in the figure) and the measurement of the related<br />

hydraulic properties in lab experiments; ii)<br />

description of the mesoscopic heterogeneity inside<br />

the horizons by an estimated covariance function<br />

in the A and C horizon; iii) modelling earthworm<br />

burrows in the middle, compacted horizon (B)<br />

by a model which mimics the formation of these<br />

macropores.<br />

As a result we obtain the continuous parameter<br />

field (hydraulic properties) of the entire<br />

experimental domain. Hence, the 3D velocity<br />

field of water could be calculated by<br />

solving Richards’ Equation numerically. Subsequently,<br />

solute transport was simulated assuming<br />

a convection-dispersion type of transport locally.<br />

Our model predicted the main characteristics<br />

of the experiment. It demonstrates that a rough<br />

description of the structure together with a rough<br />

measurement/estimation of the related material<br />

properties can be sufficient to come up with reliable<br />

predictions.<br />

Outlook/Future work The further development<br />

of non-invasive techniques to measure the<br />

heterogeneous structure of the subsurface, together<br />

with an better understanding of structure<br />

forming processes will improve our ability to quantitatively<br />

understand water flow and solute transport<br />

in soil.<br />

Main publication Vogel et al. [2005b]


3.1. SOIL PHYSICS 129<br />

3.1.8 Unsaturated Flow in Strongly Heterogeneous Porous Media<br />

Participating scientist Olaf Ippisch, Interdisciplinary Center for Scientific Computing<br />

Abstract Numerical models for the simulation of flow and transport in strongly heterogeneous<br />

porous media have been developed and optimized for speed, robustness and usability. The models<br />

were used to simulate laboratory and field experiments and were used for parameter estimation from<br />

multi-step outflow experiments.<br />

Figure 3.8: Simulation of water infiltration in a macroporous soil<br />

Background Natural porous media are often<br />

strongly heterogeneous. This can influence the<br />

flow patterns considerably, resulting in preferential<br />

flow or macropore flow which have to be taken<br />

into account to get reliable predictions of solute<br />

transport. One way to handle this problem is the<br />

use of homogenization approaches to get a set of<br />

effective parameters for the porous medium as a<br />

whole. However, if the heterogeneous structures<br />

are large in comparison to the scale of interest this<br />

is no longer possible. An alternative strategy is<br />

the determination of the soil structure (e.g. with<br />

x-ray tomography, geoelectrics, georadar) and the<br />

direct simulation of the flow field. Special numerical<br />

problems arise for parameter fields changing on<br />

a very small scale with sometimes highly nonlinear<br />

parameter functions resulting in poor convergence<br />

of the linear and nonlinear solvers.<br />

Funding <strong>Institut</strong>e for Informatics, University of<br />

Heidelberg<br />

Methods and results The developed model<br />

µϕ uses the Levenberg-Marquardt-Algorithm for<br />

parameter estimation with sensitivities derived by<br />

external numerical differentiation. The forward<br />

model solves Richards’ equation or twophaseflow<br />

equations using a cell-centered finite-volume<br />

scheme with full-upwinding in space and an implicit<br />

Euler scheme in time. Linearization of the<br />

nonlinear equations is done by an inexact Newton-<br />

Method with line search. The linear equations are<br />

solved with an algebraic multigrid solver. For the<br />

time solver the time step is adopted automatically.<br />

Brooks-Corey and van Genuchten parametrizations<br />

as well as cubic splines can be used for the<br />

hydraulic functions. Solute transport was discretized<br />

using a higher-order Godonov method<br />

with a minmod slope limiter for the convective<br />

part and a finite-volume scheme for the diffusive<br />

term. It is currently limited to steady-state flow<br />

conditions.<br />

Outlook/Future work The model will be<br />

ported to the new base library Dune which facilitates<br />

the parallelization and the use of different<br />

grid types. Parameter estimation is currently expanded<br />

to evaporation experiments. The stability<br />

and usability of the twophase will be improved<br />

and the solute transport model expanded to nonsteady-state<br />

flow conditions.<br />

Main publications Vogel et al. [2005b]


130 CHAPTER 3. TERRESTRIAL SYSTEMS<br />

3.1.9 Assessing temporal changes in volumetric soil water content from<br />

ground-penetrating radar profiles<br />

Participating scientists Ute Wollschläger, Kurt Roth<br />

Abstract We investigated the applicability of ground-penetrating radar (GPR) to estimate temporal<br />

changes of volumetric soil water content at the field scale. Water contents calculated from a time series<br />

of GPR reflections are compared to values derived independently from time domain reflectometry<br />

(TDR) measurements. We found that the results of both methods are well comparable.<br />

volumetric water content<br />

0.4<br />

0.3<br />

0.2<br />

0.1<br />

0<br />

-0.1<br />

-0.2<br />

-0.3<br />

-0.4<br />

2<br />

1<br />

Feb. March April May June July August Sept.<br />

50 100 150<br />

day of year 2004<br />

200 250<br />

0 m...0.8 m, calc. GPR<br />

0 m...0.8 m, calc. TDR<br />

0.8 m...1.65 m, calc. GPR<br />

0.8 m...1.65 m, calc. TDR<br />

1 0 m...0.8 m, meas. mean TDR<br />

2 0.8 m...1.65 m, meas. mean TDR<br />

Figure 3.9: Mean volumetric water contents of the sections 0...0.80 m (1) and 0.80...1.65 m (2)<br />

calculated from TDR data and temporal changes calculated from GPR and TDR measurements for a<br />

1D soil profile. Changes in water content derived from both methods coincide well for both soil sections<br />

demonstrating the potential of the GPR method to estimate volumetric water contents non-invasively<br />

at much larger scales.<br />

Background Measurements of volumetric soil<br />

water content are essential for many scientific,<br />

agricultural and economic questions since it is an<br />

important parameter for plant growth, groundwater<br />

recharge calculations and the local climate. In<br />

contrast to classical methods like TDR or thermogravimetric<br />

measurements, GPR surveys are noninvasive<br />

and can easily be applied on scales of a<br />

few hundreds of meters.<br />

Funding DFG, project RO 1080/8-2<br />

Methods and results At the Grenzhof Test<br />

Site, a time series of GPR reflection measurements<br />

was taken along a fixed transect to determine temporal<br />

changes in volumetric soil water content at<br />

the field scale. For one single trace volumetric<br />

water contents were calculated from the two-way<br />

travel times of two reflections at known depths<br />

of 0.80 m and 1.65 m using the Complex Refractive<br />

Index Method (CRIM). The measurements<br />

were compared to volumetric water contents derived<br />

from independent TDR measurements from<br />

several depths at nearby soil profiles (fig. 1). During<br />

summer 2004 several wetting and drying cycles<br />

were observed in the upper soil section. The corresponding<br />

changes in volumetric soil water content<br />

were detected equally well by both methods.<br />

In the lower soil section water content remains<br />

quite stable which is again shown by both methods.<br />

This investigation demonstrates the power<br />

of GPR to determine volumetric water contents<br />

in soils at the field scale down to a depth of several<br />

meters.<br />

Outlook/Future work GPR time series will<br />

be measured at a scale of a few 100 m. We will use<br />

an array of two GPR antennas which allows to determine<br />

the depth of occuring reflections without<br />

the necessity of ground-truth information from<br />

soil profiles or drillings. The gained data will be<br />

used as important information for the modelling<br />

of the water dynamics in the vadose zone.<br />

Main publication Wollschläger & Roth [2005]


3.1. SOIL PHYSICS 131<br />

3.1.10 Monitoring Field Tracer Experiment with Ground Penetrating Radar<br />

and Time Domain Reflectometry<br />

Participating scientist Carolin Ulbrich, Ute Wollschläger, Kurt Roth<br />

Abstract We explored the feasibility of Ground Penetrating Radar to non-destructively monitor<br />

solute movement in natural soils at the field scale. In a weekly radar time series the displacement<br />

of a CaCl2-tracer was monitored. The test site was instrumented with Time Domain Reflectometry<br />

probes in several depths to measure soil water content and electric conductivity.<br />

Background On its way down from the soil surface<br />

to aquifers, water passes through soil that<br />

acts as a filter. The transport and decomposition<br />

of fertilizers and contaminants determines the<br />

quality of groundwater.<br />

The interaction of this complex system cannot<br />

be calculated exactly. So appropriate restrictions<br />

have to be chosen and abstract models developed<br />

in order to get a quantitative description of a<br />

few important aspects which can be used for estimations.<br />

To assess the applicability of a certain<br />

model one has to verify its predictions with experiments.<br />

At small scales (O(1 m)) there exist numerous validation<br />

methods, but most of them cannot be<br />

implemented at larger scales (O(100 m)) because<br />

they are destructive or too time-consuming.<br />

The aim of this work was to test Ground Penetrating<br />

Radar (GPR) as a new technique to<br />

non-destructively monitor subsurface solute transport<br />

processes. It was compared with Time Domain<br />

Reflectometry (TDR) measurements and<br />

with data from soil sampling. Model predictions<br />

of solute transport on this scale were applied.<br />

Methods and results At the Grenzhof Test<br />

Site, a conservative tracer fluid that absorbs the<br />

radar wave was spread on a streak that crosses<br />

GPR transects vertically. The transport of the<br />

absorbing fluid was monitored weekly with a GPR<br />

antenna along these transects. At the end of the<br />

experiment a trench was excavated and sampled<br />

along the streak. The samples were analyzed with<br />

traditional methods to verify the radar data set.<br />

In addition, a TDR time series was acquired in<br />

the same area in three depths. The comparison to<br />

the excavation samples showed that TDR can be<br />

used to monitor tracer concentration at the instru-<br />

Figure 3.10: GPR radargram. Amplitudes of<br />

single radar pulses are plotted versus their travel<br />

times at the distances where they have been<br />

acquired. The recorded signals before ≈ 15 ns<br />

originate from air- and ground-waves that travel<br />

through the air and along the soil surface, respectively.<br />

The salt tracer was applied between<br />

5.8 m and 7.8 m. It absorbs the radar signal.<br />

mented depth in a semi-quantitative approach.<br />

The absorption effect of the highly concentrated<br />

salt tracer was clearly visible in the GPR surveys.<br />

Figure 3.10 shows a radargram acquired<br />

one month after the application of the tracer. Reflections<br />

at layer borders, visible in the GPR surveys<br />

that were taken before the application of the<br />

tracer, disappeared when the signal was absorbed<br />

by the tracer pulse. The reflections could be detected<br />

again when the tracer pulse passed the reflector.<br />

Obviously, the spatial resolution and accuracy is<br />

much better in traditional sampling experiments,<br />

but the effort there is enormous and the destructive<br />

manner impedes large scale surveys. TDR<br />

provides point measurements with good accuracy<br />

and excellent temporal resolution. GPR holds the<br />

promise to large scale experiments with good temporal<br />

resolution but coarse spatial resolution. A<br />

significant further effort is required to make it<br />

quantitative, however.<br />

Outlook/Future work A solute transport experiment<br />

is planned to be performed on the Grenzhof<br />

Test Site. At a scale of about 300 m tracer<br />

will be applied on small areas and the displacement<br />

will be monitored with GPR and TDR. The<br />

tracer distribution will be tracked in addition by<br />

permanent electric resistivity measurements. This<br />

will help to achieve a better understanding of<br />

transport processes and to further develop the<br />

methods of GPR and TDR monitoring of tracer<br />

movement.<br />

Main publication Ulbrich, Carolin, Diplomarbeit,<br />

<strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong><br />

Heidelberg, October 2005


132 CHAPTER 3. TERRESTRIAL SYSTEMS<br />

3.1.11 Efficient reconstruction of dispersive dielectric profiles using TDR<br />

Student assistant Patrick Leidenberger, Benedikt Oswald, Kurt Roth<br />

Abstract Time Domain Reflectometry (TDR) has become an indispensable technique for measuring<br />

the water content of soils. We use a numerical model for TDR signal propagation in dispersive dielectric<br />

materials. We couple this model with a genetic algorithm to invert measured TDR traces. To make<br />

this approach more efficient we use hierarchical spatial resolution.<br />

Figure 3.11: Reconstruction of a measured TDR trace (Grenzhof test site, Heidelberg; 30cm three-rod<br />

probe); reflection coefficient ρ vs. time. The ohmic and dispersive dielectric profiles (spatial resolution<br />

3.75cm) for the calculated trace are generated with a hierarchical genetic algorithm.<br />

Background A TDR instrument transmits a<br />

fast rise time pulse on a TDR probe. The probe<br />

usually consists of parallel conductors. Variations<br />

of impedance along the probe causes a partial<br />

reflection of the signal, which is measured.<br />

Furthermore the conductivity and the frequencydependent<br />

dielectric properties between the conductors<br />

of the probe have an affect on the measured<br />

signal.<br />

In this study we want to extract the dielectric<br />

parameters from TDR traces measured at the<br />

Grenzhof test site at Heidelberg to get the water<br />

content. Therefore we reconstruct hierarchical the<br />

spatial distributed dielectric parameters along the<br />

probe with a genetic algorithm.<br />

Funding Deutsche Forschungsgemeinschaft<br />

(Project No. 1080-8/2)<br />

Methods and results We have implemented<br />

a explicite time domain solver for the transmission<br />

line equations (3.3) and (3.4) that uses Debye<br />

model for dispersive media.<br />

∂v<br />

∂x<br />

∂i<br />

∂x<br />

�<br />

= − R ′ �<br />

′ ∂<br />

+ L i (3.3)<br />

∂t<br />

�<br />

= − G ′ �<br />

′ ∂<br />

+ C v (3.4)<br />

∂t<br />

The transmission line equations with piecewise<br />

constant parameters describes a TDR probe. We<br />

couple this solver with a genetic algorithm, in order<br />

to reconstruct the dispersive dielectric and<br />

ohmic profiles along the TDR probe. The genetic<br />

algorithm generates a population with different individuals<br />

(a number of different sets of profiles).<br />

For every individual we calculate a synthetic TDR<br />

trace and compare it with the measured trace.<br />

Then the new population is created from the old<br />

one by crossing the best individuals and random<br />

mutation. We use the genetic approach here, because<br />

the error landscape contains a lot of local<br />

minima.<br />

We implement a hierarchical spatial reconstruction<br />

of the profiles for more efficiency. Therefor<br />

we start with a coarse spatial resolution of the<br />

parameter profile. If the calculated TDR traces<br />

from new individuals do not match better to the<br />

measured trace for a while we increase the spatial<br />

resolution, by cutting old intervals into halves.<br />

This method does not only speed up the profile reconstruction<br />

process but also leads to a smoother<br />

parameter profile.<br />

Outlook/Future work The code will be tested<br />

on TDR traces measured with long probes (1m or<br />

more). Such a long, vertical installed TDR probe<br />

will provide a lot of informations about grounds<br />

properties in a simple way.<br />

Main publication Leidenberger, P., Oswald,<br />

B. and Roth, K. (2005). Efficient reconstruction<br />

of dispersive dielectric profiles using time domain<br />

reflectometry (TDR). Hydrology and Earth System<br />

Sciences Discussions, 2 (4), 1449-1502.


3.1. SOIL PHYSICS 133<br />

3.1.12 3D Full-wave, electromagnetic model of ground penetrating radar<br />

systems<br />

Participating scientist Benedikt Oswald<br />

Abstract Ground penetrating radar (GPR) has been increasingly used in hydrological applications<br />

for subsurface structure investigation. The size of structures that can be resolved is intimately related<br />

to the relevant wavelength of the GPR signal. A finite element time domain 3-dimensional<br />

electrodynamics code has been implemented for studying GPR signal propagation.<br />

+Y[m]<br />

+Y[m]<br />

3<br />

3<br />

2<br />

2<br />

1<br />

1<br />

+Z[m]<br />

2<br />

1<br />

0 0<br />

+Z[m]<br />

2<br />

1<br />

0 0<br />

1<br />

1<br />

2<br />

2<br />

3<br />

+X[m]<br />

-6.08<br />

-12.83<br />

-19.59<br />

-26.34<br />

-33.10<br />

+X[m]<br />

3 -39.85<br />

-46.61<br />

-53.36<br />

pdelta_310_340tsno1400.job.cmp<br />

Figure 3.12: An electromagnetic wave is launched<br />

from a horizontal dipole antenne on the soil surface<br />

(upper side of green regon) and scattered<br />

off 2 dielectric objects (2 yellow regions) buried<br />

in the underground (inside green region); lower<br />

plot: dielectric parameter distribution modeling<br />

two spheres; upper plot: contour plot of the normalized<br />

electric field intensity [dB] for timestep<br />

1400 of the simulation.<br />

Background Increasing GPR resolution requires<br />

shorter wavelength λ which demands higher<br />

frequency f. Due to attenuation of the GPR signal<br />

proportional to frequency, there is a tradeoff<br />

between resolution and penetration depth. For<br />

increasing resolution a full-wave electromagnetic<br />

analysis of GPR signal propagation is essential.<br />

There is evidence that sub-wavelength structures<br />

may be manifest in the radargram. We will use<br />

a 3-dimensional, full-wave model of a simplified<br />

GPR system. We adopt a near field electromag-<br />

8.99<br />

7.86<br />

6.74<br />

5.61<br />

4.49<br />

3.36<br />

2.24<br />

1.11<br />

[dB]<br />

[-]<br />

netic approach, originally [Ohtsu & Kobayashi,<br />

2004] employed in scanning near field optical microscopy<br />

(SNOM). We study the GPR’s response<br />

to sub-wavelength sized objects and investigate<br />

the capability of GPR to resolve those structures.<br />

Funding IUP<br />

Methods and results We have implemented a<br />

3-dimensional finite element code to solve the electric<br />

field vector wave equation (3.5) in the time<br />

domain [Oswald & Roth, 2005a].<br />

∇ × 1<br />

µ ∇ × E + σ ∂E<br />

∂t + ɛ∂2 E<br />

∂2 = −∂J<br />

t ∂t<br />

(3.5)<br />

Locally refined, tetrahedral grids are used to describe<br />

the geometry of the GPR configuration;<br />

this allows for detailed models of delicate geometrical<br />

features. In order to model open region<br />

problems we employ an absorbing boundary<br />

condition (ABC). The code has been validated<br />

on a Hertzian dipole radiating into free space.<br />

We study a simplified GPR configuration of two<br />

spherical objects separated by a sub-wavelength<br />

distance, 0.3 m in the shown example, buried in<br />

the subsurface. The distance between the sphericals<br />

is small with respect to the dominang wavelength<br />

λ. The dielectric structure of the buried<br />

spheres is mapped into the electric field observed<br />

on the surface.<br />

Outlook/Future work The code will be used<br />

in order to study more complicated underground<br />

structures; in particular we want to investigate<br />

synthetical radargram generation in order to compare<br />

those to measured radargrams. We will use<br />

dielectric material properties measured from real<br />

soil [Oswald et al. , 2006] to obtain a realistic<br />

model. This will be one of the first steps towards<br />

the challenge of GPR full-wave inversion.<br />

Main publication Oswald et al. [2006]


134 CHAPTER 3. TERRESTRIAL SYSTEMS<br />

3.1.13 Simulation and Observation of an Evanescent Wave in Ground Penetrating<br />

Radar Applications<br />

Participating scientist Holger Gerhards, Benedikt Oswald<br />

Abstract A radiating dipole near a single boundary layer was simulated to observe air and ground<br />

wave occurring in Ground Penetrating Radar applications. A semi-analytical approach to solve<br />

Maxwell’s equations in frequency domain with Green’s functions was used. The evanescent characteristic<br />

of the ground wave in air was demonstrated theoretically and experimentally.<br />

x<br />

air<br />

soil<br />

(4)<br />

(3)<br />

(1)<br />

antenna<br />

z<br />

(2)<br />

Background Ground Penetrating Radar<br />

(GPR) is a fast and nondestructive electromagnetic<br />

method to do near subsurface explorations<br />

to estimate soil water content. Reflections are<br />

measured, which occur at boundaries with a dielectric<br />

contrast. Because the relative dielectric<br />

permittivity (εw ≈ 81) of water is much higher<br />

than the soil matrix (εs ≈ 3) in the used frequency<br />

range between 0.1 to 1.0 GHz and assuming that<br />

high water content changes coincides with soil<br />

layers, temporal changes of water content can be<br />

easily detected analyzing travel times.<br />

As shown in Fig. 3.13 for a two layer (air/soil)<br />

model a direct wave from transmitter to receiver<br />

in air and another in the soil can be observed. The<br />

measured ground wave in the air has an evanescent<br />

character, which means, that its amplitude<br />

decays exponentially with the height of the receiving<br />

antenna over the soil. The knowledge about<br />

this phenomena can help to separate the interfering<br />

air and ground waves or to obtain information<br />

about the dielectric properties of the soil surface.<br />

Funding DFG RO 1080 / 10-1<br />

Methods and results A radiating dipole<br />

within a two layer medium was modeled using a<br />

semi-analytical approach based on a spectral decomposition<br />

of the Green’s functions in frequency<br />

domain. The obtained electric field components<br />

were transformed into time domain to be able to<br />

compare the simulation with field measurements.<br />

Figure 3.13: Propagation modes at a single<br />

boundary layer; (1) and (2) spherical wave like<br />

propagation modes in the according material,<br />

(3) ground wave coupling in air (evanescent<br />

wave), (4) air wave coupling in soil (lateral/head<br />

wave)<br />

The exponential decay and its frequency dependence<br />

can be shown by analyzing the amplitudes<br />

of the ground wave wavelet and its shape with<br />

increasing height above the soil.<br />

Analogous to the simulation experiments were<br />

arranged, where the evanescent behavior of the<br />

ground wave was verified and therefore validates<br />

the semi-analytical approach. Furthermore, it was<br />

shown, how far the ground wave interferes with<br />

the air wave.<br />

To obtain insight on the parameters that determine<br />

the attenuation, an equation was derived<br />

from the plane wave approach used in optics. The<br />

dependency on frequency and dielectric contrast<br />

was obtained, which can be qualitatively shown<br />

with the simulated and measured time signals.<br />

Outlook/Future work A frequency analysis<br />

must be applied to check the derived frequency<br />

dependence for experimental data. If air and<br />

ground waves interfere with each other, a quantitative<br />

separation must be developed, such as using<br />

a wavelet analysis. Furthermore, the semianalytical<br />

approach will be extended to simulated<br />

multilayered models, which may help to understand<br />

the depth-dependency of the ground wave<br />

when a near subsurface water content gradient exists.<br />

Main publication Gerhards, Holger, Diplomarbeit,<br />

<strong>Universität</strong> Jena, 2004


3.1. SOIL PHYSICS 135<br />

References<br />

Bayer, A. 2005. X-ray attenuation techniques to explore the dynamics of water in porous media. PhD<br />

thesis, University of Heidelberg.<br />

Bayer, A., Vogel, H.-J., & Roth, K. 2004. Direct measurement of the soil water retention curve<br />

using X-ray absorption. Hydrology and Earth System Sciences Discussion, 8(1), 2–7, SRef–ID:<br />

1607–7938/hess/2004–8–2.<br />

Bayer, A., Vogel, H.-J., Ippisch, O., & Roth, K. 2005. Do effective properties for unsaturated weakly<br />

layered porous media exist? An experimental study. Hydrology and Earth System Sciences Discussion,<br />

2, 1087–1105, SRef–ID: 1812–2116/hessd/2005–2–1087.<br />

Bittelli, M., Flury, M., & Roth, K. 2004. Use of dielectric spectroscopy to estimate ice content in<br />

frozen porous media. Water Resour. Res., 40, W04212, doi:10.1029/2003WR002343.<br />

Braun, H., Christl, M., Rahmstorf, S., Ganopolski, A., Mangini, A., Kubatzki, C., Roth, K., &<br />

Kromer, B. 2005. Possible solar origin of the 1,470-year glacial climate cycle demonstrated in a<br />

coupled model. Nature, in press, doi: 10.1038/nature04121.<br />

Herzog, A. 2005. Free Parameterisation of Soil Hydraulic Properties. Diplomarbeit, University of<br />

Heidelberg.<br />

Leidenberger, P., Oswald, B., & Roth, K. 2005. Efficient Reconstruction of dispersive dielectric profiles<br />

using Time Domain Reflectometry (TDR). Hydrology and Earth System Sciences Discussion, 1449–<br />

1502.<br />

Ohtsu, M, & Kobayashi, K. 2004. Optical Near Fields. 1 edn. Advanced Texts in Physics. Berlin -<br />

Heidelberg: Springer.<br />

Oswald, B., & Roth, K. 2005a. Electromagnetic full wave analysis of sub-wavelength sized objects in<br />

ground penetrating radar (GPR). Page 04437 of: Geophysical Research Abstracts, vol. 7. European<br />

Geosciences Union, EGU, Vienna.<br />

Oswald, B., & Roth, K. 2005b. A full-wave numerical model for the interaction of L-band electromagnetic<br />

radiation with a simplified forest-like vegetation. Page 06741 of: Geophysical Research<br />

Abstracts, vol. 7. European Geosciences Union, EGU, Vienna.<br />

Oswald, B., Doetsch, J., & Roth, K. 2006. A new computational technique for procesing transmission<br />

line measurements to determine dispersive dielectric properties. Geophysics. accepted for<br />

publication.<br />

Oswald, Benedikt, & Roth, Kurt. 2005c. Parallel 3D Finite Element Time Domain Maxwell Solver<br />

- Investigation of Ground Penetrating Radar Sub-Wavelength Resolution. Paul Scherrer <strong>Institut</strong>,<br />

Villigen. 2005, August, 25.<br />

Roth, K. 2005a. Bodenwasser: Bedeutung – Herausforderung – Messung. Eröffnungsvortrag, Soil<br />

Moisture Group, <strong>Universität</strong> <strong>Karls</strong>ruhe, 8. Juni.<br />

Roth, K. 2005b. GPR zur Quantifizierung von Transportprozessen in Böden? <strong>Institut</strong> <strong>für</strong> Geophysik,<br />

<strong>Universität</strong> Kiel, 20. Mai.<br />

Roth, K. 2005c. Measurement and Modeling of Thermal and Hydraulic Dynamics of Permafrost Soils.<br />

Dept. of Earth Sciences, Uppsala University, March 31.<br />

Roth, K., & Wollschläger, U. 2005. Field-Scale Measurement of Soil Water Content. Plenary Session<br />

at International Conference on Human Impacts on Soil Quality Attributes, Isfahan, Iran, September<br />

12–16.<br />

Roth, K., Schulin, R., Flühler, H., & Attinger, W. 1990. Calibration of time domain reflectometry<br />

for water content measurement using a composite dielectric approach. Water Resour. Res., 26(10),<br />

2267–2273.<br />

Roth, K., Wollschläger, U., Cheng, Z., & Zhang, J. 2004. Exploring Soil Layers and Water Tables<br />

with Ground-Penetrating Radar. Pedosphere, 14(3), 273–282.


136 CHAPTER 3. TERRESTRIAL SYSTEMS<br />

Roth, K., Boike, J., & Vogel, H.-J. 2005. Quantifying Permafrost Patterns using Minkowski Densities.<br />

Permafrost and Periglacial Processes, 16, 277–290, doi: 10.1002/ppp.531.<br />

Stöhr, M., & Roth, K. 2005. Gradient-based estimation of local parameters for flow and transport in<br />

heterogeneous porous media. Water Resour. Res., 41, 1–14, W08401, doi:10.1029/2004WR003768.<br />

Topp, G. C., Davis, J. L., & Annan, A. P. 1980. Electromagnetic determination of soil water content:<br />

Measurement in coaxial transmission lines. Water Resour. Res., 16, 574–582.<br />

Ulbrich, C. 2005. Monitoring Field Tracer Experiment with Ground Penetrating Radar and Time<br />

Domain Reflectometry. Diplomarbeit, University of Heidelberg.<br />

Vogel, H.-J. 2005a. From Pore- to Continuum-Scale Understanding of Flow and Transport Processes<br />

in Porous Media. Keynote paper, SSSA-Annual Meeting, November 7-11, 2005, Salt Lake City,<br />

USA.<br />

Vogel, H.-J. 2005b. Hierarchies of flow and transport in soil. Keynote paper, GFHN, 29emes journees,<br />

November 24-25, 2004, Grenoble, France.<br />

Vogel, H.-J. 2005c. Modeling the heterogeneous structure of soil to predict flow and transport. SIAM<br />

Conference on Mathematical and Computational Issues in the Geosciences, June 7-10, 2005, Avignon,<br />

France.<br />

Vogel, H.-J., Tölke, J., Schulz, V. P., Krafczyk, M., & Roth, K. 2005a. Comparison of a Lattice-<br />

Boltzmann Model, a Full-Morphology Model, and a Pore Network Model for Determining Capillary<br />

Pressure-Saturation Relationships. Vadose Zone J., 4, 380–388, doi: 10.2136/vzj2004.0114.<br />

Vogel, H.-J., Cousin, I., Ippisch, O., & Bastian, P. 2005b. The dominant role of structure for<br />

solute transport in soil: Experimental evidence and modelling of structure and transport in a<br />

field experiment. Hydrology and Earth System Sciences Discussion, 2, 2153–2181, SRef–ID: 1812–<br />

2116/hessd/2005–2–1.<br />

Vogel, H.-J., Samouelian, A., & Ippisch, O. 2005c. Modeling structure to predict flow and transport.<br />

Gesellschaft <strong>für</strong> Angewandte Mathematik und Mechanik, 76th Annual Scientific Conference, March<br />

28 - April 1, 2005, Luxembourg.<br />

Vogel, H.-J., Hoffmann, H., & Roth, K. 2005d. Studies of crack dynamics in clay soil. I. Experimental<br />

methods, results, and morphological quantification. Geoderma, 125, 203–211.<br />

Vogel, H.-J., Hoffmann, H., Leopold, A., & Roth, K. 2005e. Studies of crack dynamics in clay soil.<br />

II. A physically based model for crack formation. Geoderma, 125, 213–223.<br />

Wollschläger, U., & Roth, K. 2004. Estimating the three-dimensional hydraulic structure of soils from<br />

ground-penetrating radar measurements. Pages 501–504 of: Proceedings of the 10th International<br />

Conference on Ground Penetrating Radar, Delft.<br />

Wollschläger, U., & Roth, K. 2005. Estimation of temporal changes of volumetric soil water content<br />

from ground-penetrating radar reflections. Subsurf. Sens. Technol. Appl., 6(2), doi: 10.1007/s11220–<br />

005–0007–y.<br />

Yu, Q., Shi, C., Niu, F., He, N., & Roth, K. 2005. Analysis of temperature controlled ventilated<br />

embankment. Cold Reg. Sci. Technol., 42, 17–24, doi:10.1016/j.coldregions.2004.11.004.


3.2. ICE AND CLIMATE 137<br />

3.2 Ice and Climate<br />

Names of group members<br />

Isabel Bengel, diploma student<br />

Felix Jahn, diploma student<br />

Barbara May, diploma student<br />

Christine Offermann, diploma student<br />

Dipl.Phys. Markus Pettinger, PhD student<br />

Dipl.Phys. Martin Schock, PhD student<br />

Dr. Dietmar Wagenbach, head of group<br />

Overarching topic, main methods and specific objectives Among all paleo-archives, only<br />

non-temperated glaciers basically allow the reconstruction of climate as well as of environmental<br />

records. Appropriate ice core studies may thus allow to tackle the crucial problem about the mutual<br />

relationships between changes of climate and bio-geochemical cycles through a retrospective approach.<br />

Figure 3.14: Drilling down to bedrock at Colle Gnifetti (Monte Rosa 4500m a.s.l.) September 2005.<br />

View on the exposed situation of the drill camp near the ice-cliff (dome drilling tent at upper right<br />

rim). Picture: Olaf Eisen<br />

In this context, the ’Ice and Climate’ group concentrates on ice core investigations by deploying the<br />

following species, backed up by standard physical ice properties:<br />

• water-isotopomeres δ 18 O- δD (thermometry)<br />

• various particulate key species as mineral dust, major ions, organic carbon (bio-geochemical<br />

cycles),<br />

• natural radionuclides as terrestrial 210 Pb, cosmogenic 10 Be, 3 H, 36 Cl (solar variability)and on<br />

3 He, 4 He isotopes (basal layer dynamics).<br />

Apart from joint activities within polar ice core studies, emphasis is thereby on the independent<br />

exploration of non-temperated alpine glaciers. Such small scale drill sites are unique in supplementing<br />

high latitude ice core findings, though reliable atmospheric signals would be much more difficult<br />

to elucidate here (Preunkert et al., 2000). In addition to ice core analyses, deserving application<br />

of novel techniques and species (Ruth et al., 2003), also process-oriented field studies are regularly<br />

performed. These specific activities are aimed at understanding the transfer of the atmospheric signals<br />

into the glacier archive as well as at constraining their basic glaciological embedding conditions (as e.g.


138 CHAPTER 3. TERRESTRIAL SYSTEMS<br />

controlled by the near surface and near bed-rock glacier dynamics). Based on external collaborations,<br />

dedicated atmospheric observations are deployed here at various alpine (Preunkert and Wagenbach,<br />

1998) and Antarctic sites (Wagenbach et al. 1998, Piel et al. 2005, which also include isotopic<br />

fingerprints of aerosol samples ( 15 N, 14 C, 26 Al). Within the glaciological issue, joint efforts range<br />

from ground penetrating radar soundings of the internal stratigraphy in alpine glaciers (Eisen et al.<br />

2003) and related glacio-meterological and glacio-chemical surveys, to the prospection of novel dating<br />

techniques ( 3 He/ 4 He (Friedrich, 2003), 14 C, 26 Al/ 10 Be).<br />

Overview on principal activities and achievements<br />

Alpine research<br />

a) EU- ALP-IMP related: Long term isotope records from two deep Mt. Blanc cores could be added<br />

to the already existing array of respective Monte Rosa records, enhancing the significance in the<br />

reconstruction of climate related changes (see 3.2.4). Site selection study of ideal drill site for high<br />

resolution records back to 1000 years by radar tracking of the internal layering by University Zürich<br />

(Böhlert, 2005) and drilling there to bedrock in collaboration with KUP of University Bern could be<br />

successfully achieved. First estimates indicate a net surface accumulation of the new site, significantly<br />

lower than 15 cm water per year, which may offer a relatively high time resolution in the bottom<br />

core section. A further intensive field campaign for sampling a special non-temperated ice cap at<br />

lower altitude was performed in collaboration with university Zürich, in order to prospect the basic<br />

stratigraphycal properties of this ice body (see 3.2.1) .<br />

b) EU-CARBOSOL project related: The first continuous records into the pre-industrial area of dissolved<br />

organic carbon (DOC) could be established (partly in seasonal resolution) (see 3.2.5). Also<br />

aimed at the long term change of the organic fraction of the aerosol body, the first radiocarbon investigations<br />

on european wide aerosol samples could be accomplished after final revision of the sample<br />

preparation line (see 3.2.2).<br />

Antarctica<br />

a) Related to EPICA: Field sampling of bottom core for He-isotope analyses could be accomplished<br />

at Berkner Island and at EPICA Dome C (actually the oldest ice available) drill sites. Respective<br />

mass spectrometric analyses by the ”Groundwater and Paleoclimate” group, along with noble gas ice<br />

core samples obtained from the previous campaigns are expected to come up in the near future.<br />

Investigation of the air firn transfer of 10 Be (and associated host particles) were extended from investigations<br />

at the central EPICA DML drill site(Piel et al. 2005) by a bi-annual record from a recent<br />

firn core obtained from coastal Berkner Island. In this context long term observations of atmospheric<br />

radionuclides at Neumayer Station were regularly continued (see 3.2.3).<br />

b)The Lake Vostok: Additional ice samples of the Vostok bottom ice core (accreted from Lake Vostok)<br />

as well as meteoric reference ice were obtained from LGGE-CRNS. Grenoble and analysed for dissolved<br />

organic Carbon, confirming the outstanding low DOC level, already obtained in previous pilot analyses<br />

(Bulat et al.2004) (see 3.2.5)<br />

c) New developments focussed on the extension of automatic aerosol sampling in central Antarctica<br />

and on the prospection of the 26 Al/ 10 Be dating tool, to be deployed for very old ice. (see 3.2.6)<br />

Novel activities envisaged in the following year Launching a radiocarbon dating project focussing<br />

on various non-temperated Alpine ice bodies (with VERA and University Zürich).<br />

Supplementing continuous flow ice core analyses by a screening method for the total gas content, as<br />

to infer the melt-layer stratigraphy (with Groundwater and Paleoclimate Group)<br />

Pilot studies on the Little Ice Age variability of 10 Be possibly archived in a new sediment core recovered<br />

from the well explored high alpine Schwarzsee ob Sölden (with University Innsbruck and Heidelberg<br />

Academy of Sciences)<br />

Re-designing of the Air Chemistry Observatory at the Antarctic Neumayer Station III (with AWI and<br />

the Carbon Cycle Group)<br />

Funding and major cooperations Funding relayed on the EU-projects CARBOSOL (Anthropogenic<br />

change of organic carbon aerosol in West- Europe)and ALP-IMP (Climate variability in the<br />

greater Alpine region), the AWI-Cooperation contract (Investigation of ice cores and aerosol of polar


3.2. ICE AND CLIMATE 139<br />

regions) and on an Austrian Research Fund project jointly with VERA ( 26 Al- 10 Be investigations). Important<br />

logistical support was obtained from the ESF-EU core project EPICA (European Ice Drilling<br />

in Antarctica).<br />

Vital long term collaborations (also operating outside funding projects) comprised joint activities<br />

with:<br />

• Alfred Wegener <strong>Institut</strong>e for Polar and Marine Research (various polar investigations),<br />

• Laboratoire de Glaciolocique et Geophisique-CRNS, Grenoble (alpine ice cores and Lake Vostok),<br />

• Geographical <strong>Institut</strong>e of the University Zürich (alpine glaciology and glacio-meteorology)<br />

• Klima und <strong>Umweltphysik</strong>, University Bern (ice core drilling and analyses),<br />

• VERA-laboratory, <strong>Institut</strong> <strong>für</strong> Isotopenforschung und Kernphysik der <strong>Universität</strong> Wien (AMSanalyses)<br />

• <strong>Institut</strong>e for Zoology and Limnology, University Innsbruck (ice biology and high alpine lake<br />

sediments),<br />

• British Antarctic Survey, Cambridge (Berkner Island Project)<br />

• <strong>Institut</strong>e for Environmental Geochemistry, University Heidelberg (trace element analyses)<br />

Internal collaboration concentrates on: the Neumayer Observatory, 14 C and radon investigations<br />

(Carbon Cycle Group), noble gas and tritium analyses (Groundwater and Paleoclimate Group) as<br />

well as on long term marine 10 Be sediment records (Heidelberger Academy of Sciences).<br />

Publications<br />

Peer Reviewed Publications<br />

1. Bulath et al. [2004]<br />

2. Legrand et al. [2005]<br />

3. Piel et al. [accepted]<br />

Other Publications<br />

1. Auer et al. [2005]<br />

2. Bigler et al. [2005]<br />

3. Dombrowski-Etchevers et al. [2005]<br />

4. Pettinger et al. [2005]<br />

5. Schock et al. [2005]<br />

6. Steier et al. [2005]<br />

7. Wegner et al. [2005]<br />

Diploma Theses<br />

1. Bengel [2005]<br />

2. May [2005]<br />

Invited Talks<br />

1. Schock et al. [2005]<br />

2. Pettinger et al. [2005]<br />

3. Wagenbach [2004]


140 CHAPTER 3. TERRESTRIAL SYSTEMS<br />

3.2.1 Glaciological pilot studies on a cold miniature ice cap<br />

Participating scientist Isabel Bengel and Wilfried Haeberli ∗<br />

∗ Glaciology and Geomorphodynamics Group, Geography Department, University of Zürich<br />

Abstract The study deals with the glacio-chemical characterisation of a high alpine miniature ice<br />

cap (Piz Murtèl, 3433 m a.s.l., Oberengadin). Inside an ice tunnel the 210 Pb and 3 H point to<br />

ice, surprisingly less than 50 years old. On the whole, the ice body of Piz Murtèl exhibits a dust<br />

stratigraphy and distinct age distribution, but less regular than in sedimentary ice.<br />

Figure 3.15: Above: Northwest flank of Piz<br />

Murtèl (3300 m a.s.l.) seen after an intense summer<br />

ablation period with indicated 2004 samplings.<br />

Below: Shallow profile of 3 H (T 1/2 =<br />

10.3 a) and 210 Pb (T 1/2 = 22 a) obtained in the<br />

interior tunnel floor, showing surprisingly modern<br />

ice conditions.<br />

Background Different to high alpine cold<br />

glaciers (above 4000 m a.s.l.) the environmental<br />

information, which maybe contained in lower elevation<br />

miniature ice caps remained virtually unknown.<br />

Because of a small mass turnover and low<br />

ice motions in such ice caps a relatively high age<br />

in the order of some 1000 years may be expected<br />

(Haeberli et al., 2004). An alpine prime example<br />

for a miniature ice cap provides the Piz Murtèl<br />

(Oberengadin, Suisse) which is analysed in this<br />

study. Being non-temperate despite its low elevation,<br />

the ice cap might be used as an archive<br />

containing the history of past minimum glacier<br />

extend. The primary aim of this study was to<br />

gather basic information on the internal stratigraphy,<br />

age structure and accumulation processes<br />

by screening the isotope and chemical ice properties.<br />

Methods and results In October 2004, a continous<br />

50 m profile at the northwest flank and a<br />

shallow ice core in an artifical ice tunnel were sampled<br />

in collaboration with University of Zürich.<br />

First measurements of the variability of ice impurities<br />

have been carried out based on fast standard<br />

methods including continous profiling of particles,<br />

liquid conductivity and electrical ice conductivity.<br />

Thereby it turned out, that the mineral dust variability<br />

in the samples – although partly consisting<br />

of superimposed ice and containing ablation<br />

dirt– could be measured without essential modifications.<br />

Also the electrical method generated<br />

reproducible profiles, allowing to record the ice<br />

stratigraphy at a sub-cm resolution. Exemplary<br />

radionuclide analyses gave (as expected) a 210 Pb<br />

down slope increase but surprisingly young ice<br />

of less than 50 years ( 210 Pb and 3 H) inside the<br />

calotte. Although soluble ion components appeared<br />

to be strongly affected by elution, a DOC<br />

level around 200 ppb was found, making dating by<br />

14 C analyses possible. On the whole, the ice of<br />

Piz Murtèl exhibits a dust stratigraphy and spatial<br />

age distribution which is, however, modified<br />

by the untypical properties of the miniature ice<br />

cap, governed by complicated ablation / accumulation<br />

processes.<br />

Outlook/Future work Drilling into and dating<br />

of the basal layer.<br />

Main publication Bengel [2005]


3.2. ICE AND CLIMATE 141<br />

3.2.2 Constraining the anthropogenic fraction of carbonaceous aerosol by<br />

14 C-analysis<br />

Participating scientists Barbara May, Samuel Hammer and Peter Steier ∗<br />

∗ VERA Laboratory, <strong>Institut</strong> <strong>für</strong> Isotopenforschung und Kernphysik, <strong>Universität</strong> Wien<br />

Abstract A sample preparation line for 14 C analysis of aerosol filters for AMS has been revised<br />

and characterised. First analyses revealed that the European carbonaceous aerosol is of mainly recent<br />

origin, while the free tropospheric clean air condition indicates a more fossil contribution.<br />

Figure 3.16: Range of the relative contribution of<br />

fossil carbon seen in aerosol sampled during winter<br />

and summer half years at various mountain sites<br />

(Sonnblick, Austria; Schauinsland, Germany; Puy<br />

de Dôme, France). Note the significantly higher<br />

fossil carbon fraction during the relatively clean<br />

winter conditions.<br />

Background While inorganic aerosols, like sulphate,<br />

are relatively well understood regarding<br />

their anthropogenic sources and related radiative<br />

forcing implications, anthropogenic change of carbonaceous<br />

aerosol and its radiative influence are<br />

virtually unknown. Therefore, we attempted to<br />

quantify the recent versus fossil fraction of total<br />

organic carbon from European wide sampled<br />

aerosol filters by the 14 C approach. Here, 14 C<br />

measurements may allow to quantitatively distinguish<br />

between the fossil fraction, completely free<br />

of 14 C, and the recent one, carrying the present<br />

day 14 C signature of biogenic carbon. The low<br />

carbon mass and various fractionation processes<br />

associated with aerosol sample combustion make<br />

however thorough experimental efforts necessary<br />

to achieve reliable 14 C results.<br />

Funding EU CARBOSOL-project: Present<br />

and retrospective state of organic versus inorganic<br />

aerosol over Europe: Implications for climate<br />

Methods and results For analysing the 14 C<br />

signature of aerosol filters, a pilot system for controlled<br />

sample combustion in a gas stream and<br />

subsequent purification and extraction of the CO2<br />

(designed by Hammer (2003)) for δ 13 C and AMS<br />

14 C analysis (Steier et al, 2004) was optimised and<br />

characterised. It was shown, that the combustion<br />

process efficiency increases when pure oxygen is<br />

used as combustion gas. Furthermore a water cold<br />

trap is necessary in excess as well as a second combustion<br />

step (assuring the total combustion of the<br />

organic matter). The system allows to reasonably<br />

quantify a minimal carbon amount of 65 µgC<br />

with an accuracy of 10 %. The typical blank level<br />

of the entire process is found to be 63 µgC with<br />

a 14 C content close to 80 pmC (percent modern<br />

Carbon).<br />

A first systematic investigation of CARBOSOL<br />

aerosol filters, specifically selected by 210 Pb data,<br />

indicated: (1) Around 75 % of the carbonaceous<br />

aerosol is released by non-fossil sources, which appear<br />

to be rather uniformly distributed over Western<br />

Europe. (2) Under free tropospheric clean air<br />

conditions nearly one third of the carbonaceous<br />

aerosol may be ascribed to fossil sources (see Figure).<br />

An attempt to interpret these results in<br />

terms of anthropogenic emissions, considering the<br />

variable amount of bomb 14 C added by biomass<br />

burning, proved to be difficult.<br />

Outlook/Future work The system basically<br />

allows the separation of BC (black carbon) and<br />

OC (organic carbon), which may improve the interpretation<br />

in terms of anthropogenic emissions.<br />

Furthermore, upcoming ice core based CAR-<br />

BOSOL results of pre-industrial organic aerosol<br />

concentrations may allow an independent comparison<br />

of the anthropogenic contribution to present<br />

day organic aerosol levels.<br />

Main publication May [2005]


142 CHAPTER 3. TERRESTRIAL SYSTEMS<br />

3.2.3 Recent variability of the cosmogenic nuclides 10 Be and 7 Be in coastal<br />

Antarctica<br />

Participating scientists Christine Offermann, Matthias Auer ∗ and Robert Mulvaney ∗∗<br />

∗ VERA Laboratory, <strong>Institut</strong> <strong>für</strong> Isotopenforschung und Kernphysik, <strong>Universität</strong> Wien<br />

∗∗ British Antarctic Survey, Cambridge<br />

Abstract The solar activity proxy 10 Be is investigated in a firn core of coastal Antarctica (Berkner<br />

Island) along with the 10 Be and 7 Be activities, obtained from aerosol filters at Neumayer station.<br />

Data evaluation is aimed at assessing the air-firn transfer of 10 Be.<br />

Background Cosmogenic 10 Be archived in polar<br />

ice sheets provides an unique tool in reconstructing<br />

solar activity changes. Dueto various<br />

glacio-meteorological noise, the interpretation of<br />

those, latitude dependant, records remained however<br />

ambiguous . Moreover only very few 10 Be ice<br />

core findings are available from the recent (preinstrumental)<br />

era. In this context IUP started investigating<br />

10 Be in relatively recent ice-cores from<br />

different Antarctic drill sites, focussing on the 11year<br />

solar cycle and the outstanding solar minima<br />

of the last 500 years.<br />

As the influence of meteorological noise on 10 Be<br />

is barely understood and strongly depends on the<br />

drill site, investigations at the central Antarctic<br />

EPICA-DML drill site (Wegner 2003, Wegner<br />

et al. 2005) were extended to a coastal site at<br />

Berkner Island (BI) (Rohlfs, 2004). In the coastal<br />

area, also atmospheric long term observations of<br />

7 Be and 10 Be are performed by IUP at Neumayer<br />

(NM) Station, allowing comparison with concurrent<br />

10 Be firn core data with respect to the 11-year<br />

cycle.<br />

Methods and results In this thesis the still<br />

missing high resolution 10 Be firn record from<br />

coastal Antarctica should be provided by establishing<br />

a continuous bi-annual 10 Be profile from a<br />

firn core drilled for this purpose at BI. To study<br />

the glacio-meteorological influence on the air-firn<br />

transfer of 10 Be, the aerosol time series from NM<br />

was extended by the 2004 values of 7 Be concentrations<br />

and completed by missing 10 Be data of<br />

the previous years. The challenge to gain an absolute<br />

core chronology was accomplished by combining<br />

δ 18 O and Electric Conductivity Measurement(ECM)<br />

based acidity profiling, taking advantage<br />

of the seasonal variation of the data. Moreover,<br />

to employ the VERA (AMS) facility, our<br />

10 Be target-preparation procedure has been revised<br />

with respect to the final BeO handling.<br />

∆ 7 Be [fCi/scm]<br />

100<br />

50<br />

0<br />

-50<br />

7 Be at Neumayer Station, Antarctica<br />

1985 1990 1995 2000 2005<br />

year<br />

Figure 3.17: Deviation of monthly mean atmospheric<br />

7 Be activity from the total mean of 112<br />

fCi/m 3 . Note the regular variation related to the<br />

seasonal cycle. Black line: SSA derived extraction<br />

of the underlying Schwabe cycle.<br />

While inspection of the atmospheric 7 Be record<br />

reveals the expected Schwabe cycle, also found<br />

at EPICA-DML, very recently obtained 10 Be raw<br />

data from BI does not show such prominent regular<br />

changes for the first 30 years. The reason for<br />

this discrepancy is not elucidated yet.<br />

Final work Correction for interannual snow accumulation<br />

and revision of the core chronology is<br />

envisaged to gain a useful record of the short term<br />

10 Be variability at BI. Only then comparison with<br />

concurrent changes at EPICA-DML, NM and neutron<br />

monitor data would be possible. Thus, subsequent<br />

analysis for recent trends may show if the<br />

expected decrease (Solanki et al, 2004) due to high<br />

solar activity can be found in the 10 Be record.<br />

Main publications Upcoming diploma thesis


3.2. ICE AND CLIMATE 143<br />

3.2.4 Climatic significance of stable water isotope records from Alpine ice<br />

cores.<br />

Participating scientists Markus Pettinger, Susanne Preunkert ∗ , Ralph Böhlert ∗∗ and Reinhard<br />

Böhm ∗∗∗<br />

∗ LGGS - CNRS, Grenoble<br />

∗∗ Glaciology and Geomorphodynamics Group, Department of Geography, University of Zürich<br />

∗∗∗ ZAMG, Wien<br />

Abstract Upstream effects associated with local variations in snow deposition that influence long<br />

term isotopic trends recorded in Alpine ice cores were investigated. Isotope records of two Mont Blanc<br />

ice show the recent warming trend with high isotope sensitivity, whereas long term records show only<br />

weak correlation with instrumental temperature data.<br />

Figure 3.18: δ 18 O- records of a low<br />

(0.2 m w.e./yr, middle) and a high<br />

(1.1 m w.e./yr, bottom) accumulation core<br />

from the Mont Blanc summit range.<br />

Background Isotope δ 18 O and δD records from<br />

high Alpine cold glaciers may provide complementary<br />

records to polar cores, including the unique<br />

possibility to extend the 250 years instrumental<br />

climate time series only available from western<br />

Europe (Schöner et al., 2002). On the other<br />

side various glaciological constrains hamper the<br />

straightforward interpretation of alpine isotope<br />

records in terms of temperature changes. A multicore<br />

study was therefore set up to partly compensate<br />

for this basic shortcoming.<br />

Funding EU-project ALP-IMP (Multicentennial<br />

climate variability in the Alps based on<br />

Instrumental data, Model simulations and Proxy<br />

data)<br />

Methods and results To determine systematic<br />

upstream effects in the cachment area of<br />

Monte Rosa deep ice cores three shallow firn cores<br />

have been drilled along their flow line down to a<br />

reflection layer determined by radio echo sounding<br />

(as to guarantee an common time span). The<br />

systematic change in the core mean δ 18 O value<br />

along the flow line has been used to improve the<br />

overall upstream corrections. The new data exhibit<br />

in the upper region of the flowline a linear<br />

δ 18 O-accumulation relation of 1.9 � per m water<br />

equivalent. Thus, additional corrections up to<br />

0.4� to those of Keck (2001) are necessary for<br />

the long term trends recorded in Monte Rosa ice<br />

cores. A different approach was chosen for the<br />

Mont Blanc ice core in flank position. In this case,<br />

the changes with depth of the winter snow fraction<br />

induced by wind erosion was determined, but<br />

only an insignificant dependance with depth could<br />

be found.<br />

In the time span of 1920 to 1995 both new Mont<br />

Blanc ice cores show no clear correlation with instrumental<br />

temperature, wich may be due to poor<br />

dating. In contrast the recorded recent warming<br />

trend (1980-2000) exhibits ∆δ 18 O/∆T relations<br />

between 1.5 and 3 �/ ◦ C with high significance<br />

in all ice cores. Previous studies show a relation<br />

of 1.7 �/ ◦ C in the period of 1920 to 1995. Different<br />

to existing Monte Rosa records showing an<br />

odd long term trend towards lower isotope values<br />

into the medieval era, the new Mont Blanc ice divide<br />

core exhibits no such trend, but, if any, only<br />

a weak δ 18 O increase by 0.6�. The respective<br />

ice core chronology as based on a flow only model<br />

(Raymond, 1983) is however still uncertain.<br />

Future work Dating and isotopic analysis of<br />

the new Monte Rosa ice core, drilled to get high<br />

resolution records. In addition the model based<br />

dating of the low accumulation Mont Blanc ice<br />

core has to be improved by matching with known<br />

dust and volcanic horizons.<br />

Main publication Pettinger et al. [2005]


144 CHAPTER 3. TERRESTRIAL SYSTEMS<br />

3.2.5 Analyses of dissolved organic carbon (DOC) at low levels in Alpine<br />

and polar glaciers<br />

Participating scientists Martin Schock, Steffen Greilich ∗ and Jean-Robert Petit ∗∗<br />

∗ Heidelberger Akademie der Wissenschaften, Forschungsstelle Archaeometrie<br />

∗∗ LGGE-CNRS, Grenoble<br />

Abstract Deploying a novel method for ultra-low DOC analysis, DOC in high Alpine precipitation<br />

was found to be increased by a factor of 2-4 (to up to 4 · 10 −7 gC/g) since preindustrial times, wheras<br />

DOC level less than about 10 −8 gC/g are seen in Antarctic ice cores.<br />

Background The bulk quantity DOC constitutes<br />

an important part of the impurity content<br />

of non-temperated glaciers. Related retrospective<br />

studies would be highly relevant therefore in terms<br />

of radiative forcing, past atmospheric carbon cycles<br />

and englacial microbial activity. However no<br />

systematic ice core analyses of DOC were available,<br />

yet, due to unsolved contamination problems<br />

and insufficient sensitivity of conventional TOC<br />

analysers. In this context a dedicated flow injection<br />

system, based on UV induced DOC degregation<br />

has been developed (along with an appropriate<br />

decontamination procedure as to cope with the<br />

challenge to analyse ice cores, drilled in kerosene<br />

filled bore holes).<br />

Funding EU-CARBOSOL project : ”Present<br />

and Retrospective State of Organic versus Inorganic<br />

Aerosol over Europe : Implications for Climate”<br />

Methods and results Sample decontamination,<br />

(deploying partial melting or a melting<br />

probe) is shown to control the precision and<br />

quantitative detection limit (presently around<br />

5 · 10 −9 gC/g). Extensive comparison with a high<br />

temperature combustion method revealed that the<br />

UV degradation efficiency for most of the relevant<br />

DOC species seems to be close to 90% .<br />

Various high Alpine ice cores have been systematically<br />

analysed for DOC (partly in seasonal resolution),<br />

indicating a significant change by typically<br />

a factor of 2 to 4 since the pre industrial era.<br />

This presumably anthropogenic effect is however<br />

clearly lower, compared to concurrent changes of<br />

man made inorganic species, like sulphate (Preunkert<br />

et al., 2001).<br />

DOC-surveys of a cold, low elevation Alpine ice<br />

cap (Bengel, 2005), in view of radiocarbon dating<br />

of the ice body genesis via DOC indicated, that<br />

about 1 kg ice would be needed for this purpose.<br />

Most difficult in terms of reliable measurements<br />

have been Antarctic ice cores, where DOC levels<br />

approach the limit of detection. Including polar<br />

ice cores, no big difference is seen in the pre<br />

industrial DOC level between Alpine and Greenland<br />

sites, wheras an interhemispheric difference<br />

by one order of magnitude shows up with respect<br />

to Antarctica. Here, DOC analyses in accreted ice<br />

from Lake Vostok gave a mean DOC level lower<br />

by roughly a factor of 50, than previously reported<br />

by Priscu et al., (1999), giving much less room for<br />

viable micro biological activities, than hitherto assumed<br />

(Bulat et al 2004).<br />

Figure 3.19: Range of dissolved organic carbon<br />

(DOC) content in various ice bodies (including accreted<br />

ice from Lake Vostok), displayed by median<br />

as well as by 25% and 75% percentils, respectively<br />

Outlook/Future work Radiocarbon dating of<br />

the DOC fraction in Alpine ice.<br />

Main publication J.-R. Petit , J. Flückiger, M.<br />

Leuenberger, W. Haeberli, R. Psenner , Dissolved<br />

organic carbon (DOC) in ice samples from nontemperated,<br />

polar and Alpine glaciers. Geophysical<br />

Research Abstracts, Vol. 7, 08671, 2005<br />

Schock et al. [2005]


3.2. ICE AND CLIMATE 145<br />

3.2.6 Novel tools in ice core research<br />

Participating scientists Dietmar Wagenbach, Rolf Weller ∗ and Matthias Auer ∗∗<br />

∗ AWI-Bremerhaven<br />

∗∗ VERA Laboratory, <strong>Institut</strong> <strong>für</strong> Isotopenforschung und Kernphysik, <strong>Universität</strong> Wien<br />

Abstract New developments on automatic aerosol sampling in central Antarctica and on the prospection<br />

of the 26 Al/ 10 Be dating tool are reported along with their futur application.<br />

Figure 3.20: Seasonal cycle of biogenic sulfate in central Antarctica obtained by automatic aerosol<br />

samplings (left), first tropospheric 26 Al/ 10 Be ratios derived from Antarctica Neumayer (Ant), alpine<br />

Sonnblick (SBO) and Schauinsland (SIL) Station (right).<br />

Background Among various shortcomings in<br />

the interpretation of Antartic ice core records,<br />

the air-firn transfer of aerosol species as well as<br />

the age and stratigraphical properties of the basal<br />

core sections continue to provide outstanding challenges.<br />

On the one hand, this is mainly due to<br />

missing year round atmospheric aerosol observations<br />

at central Antartic drill sites and on the<br />

other, due to the missing of appropriate dating<br />

tools reaching back beyond several 100ka. a) In<br />

order to reduce the first deficit IUP developed an<br />

autonomous aerosol sampling device (ROBERTA)<br />

(Preunkert and Wagenbach 1998) to be deployed<br />

year round at the EPICA-DML drill site in the<br />

Atlantic sector of east Antartica. b) In close collaboration<br />

with the University of Vienna AMS facility<br />

(VERA) the dating deficit of very old ice<br />

samples has been tackled by exploring the feasibility<br />

of the 26 Al/ 10 Be ratio (apparent T 1/2 =1.3<br />

10 −6 a) as a radiometric chronometer.<br />

Fundings a) AWI-Cooperation Contract, b)<br />

joint project within the Austrian Research<br />

Fund(FWF).<br />

First results a) Year round, unattended running<br />

of the aerosol sampling system could be successfully<br />

achieved in close collaboration with AWI-<br />

Bremnerhaven, providing first records on the seasonal<br />

change of major ion in central Antarctica.<br />

26 Al/ 10 Be<br />

3x10 -3<br />

2x10 -3<br />

1x10 -3<br />

0<br />

ANT<br />

SBO<br />

Adding ion concentration data in sub-seasonal resolution<br />

from concurrent firn deposits along with<br />

automatic snow hight recordings may now allow to<br />

elucidate the drill site specific air-firn transfer of<br />

the ionic aerosol species. A second sampler version<br />

substantially improved with respect to the<br />

consecutive activation of the sampling units has<br />

been put in operation.<br />

b) After establishing and optimizing the 26 Alanalysis,<br />

first tropospheric 26 Al/ 10 Be ratios could<br />

be obtained from Antarctic and mid-latitude<br />

aerosol samples. The reasonable constant ratios<br />

indicate a control by atmospheric production,<br />

rather than by terrestrial or cosmic dust inputs<br />

(which is a pre-requisite for the dating application).<br />

Future work a) Possibly deploying one of the<br />

two devices at a high altitude drill site in the western<br />

Himalayans (Pamir).<br />

b) 26 Al/ 10 Be analyses will be extended to recent<br />

polar snow and glacial ice core samples and supplemented<br />

by 53 Mn (solely derived from interplanatary<br />

dust) as to obtain a quantative estimate<br />

of the IPD influence on the 26 Al variability in polar<br />

ice cores. If successful 26 Al/ 10 Be dating might<br />

be applied the first time on ice core samples (e.g.<br />

on the basal section of the EPICA Dome C core,<br />

which comprises the oldest ice recovered so far).<br />

Main publication Auer et al. [2005]<br />

SIL


146 CHAPTER 3. TERRESTRIAL SYSTEMS<br />

References<br />

Auer, M., Kutschera, W., Priller, A., Wagenbach, D., Wallner, A., & Wild, E. M. 2005 (September<br />

5-10). Atmospheric 26 Al and 10 Be as a dating tool for climate archives (Abstract). vol. The 10th<br />

International Conference on Accelerator Mass Spectrometry Berkeley, California.<br />

Bengel, I. 2005. Spurenstoffglaziologische Pilotuntersuchungen an einer kalten Miniatureiskappe.<br />

Diplomarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg.<br />

Bigler, M., Röthlisberger, R., Ruth, U., Siggaard-Andersen, M.-L., Steffensen, J. P., Hansson, M. E.,<br />

Goto-Azuma, K., Fischer, H., & Wagenbach, D. 2005. A new high-resolution chemical ice core<br />

record over the last glacial period from NGRIP. Geophysical Research Abstracts, Vol 7, 05616.<br />

Böhlert, R. 2005. Diplomarbeit, <strong>Institut</strong> <strong>für</strong> Geographie, <strong>Universität</strong> Zürich.<br />

Böhm, R., Brunetti, M., Maugeri, M., Nanni, T., & Schöner, W. 2001. Regional temperature variability<br />

in the European Alps: 1760-1998 from homogenized instrumental time series. International<br />

Journal of Climatology, 21, 1779 – 1801.<br />

Bulath, S., Alekhina, I., Blot, M., Petit, J.-R., de Angelis, M., Wagenbach, D., Lipenkov, V., Valilyeva,<br />

L., Wloch, D., Raynaud, D., & Lukin, V. 2004. DNA singature of thermophilic bacteria from the<br />

aged accretion ice of Lake Vostok, Antarctica: implications for searching for life in extreme icy<br />

environments. International Journal of Astrobiology, 3(1), 1–12.<br />

Dombrowski-Etchevers, I., Peuch, V.-H., Wagenbach, D., & Legrand, M. 2005. Validation of concentrations<br />

of lead-210 in high altitude simulated by MOCAGE. Geophysical Research Abstracts, Vol<br />

7, 09009.<br />

Eisen, O., Nixdorf, U., Keck, L., & Wagenbach, D. 2003. Alpine Ice Cores and Ground Penetrating<br />

Radar: Combined Investigations for Glaciological and Climatic Interpretations of a Cold Alpine Ice<br />

Body. Tellus, 55B(5), 1007–1017.<br />

Friedrich, R. 2003. Helium in polaren Eisschilden. Diplomarbeit, Instiut <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong><br />

Heidelberg.<br />

Haeberli, W., Frauenfelder, R., Kääb, A., & Wagner, S. 2004. Characteristics and potential climatic<br />

significance of ”miniature ice caps” (crest- and cornice-type low-altitude ice archives. Journal of<br />

Glaciology, 50(168), 129–136.<br />

Hammer, S. 2003. Einsatz von Radioisotopen zur Interpretation der raum-zeitlichen Variabilität von<br />

organischem Aerosol. Diplomarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg.<br />

Keck, L. 2001. Climate significance of stable isotope records from Alpine ice cores. Ph.D. thesis,<br />

<strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg.<br />

Legrand, M., Preunkert, S., Galy-Lacaux, C., Liousse, C., & Wagenbach, D. 2005. Atmospheric yearround<br />

records of dicarboxylic acids and sulfate at three French sites located between 630 and 4360<br />

m elevation. Journal of Geophysical Research, 110, D13302, doi:10.1029/2004JD005515.<br />

May, B. 2005. Quantification of the fossile fraction of carbonaceous aerosol by radiocarbon analysis.<br />

Diplomarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg.<br />

Pettinger, M., Keck, L., Fischer, H., Wagenbach, D., Preunkert, S., Böhm, R., Hoelzle, M., & Hoffmann,<br />

M. Leuenbergerand G. 2005. Cenntennial scale isotope thermometry from Alpine ice core<br />

records: shortcomings and challenge. Geophysical Research Abstracts, Vol 7, 07941.<br />

Piel, C., Weller, R., M.Huke, & Wagenbach, D. accepted. Atmospheric methane sulfonate and non-sea<br />

salt sulfate records at the EPICA deep-drilling site in Dronning Maud Land. Journal of Geophysical<br />

Research, 2005JD006213.<br />

Preunkert, S., & Wagenbach, D. 1998. An automatic recorder for air/firn transfer studies of chemical<br />

aerosol species at remote glacier sites. Atmospheric Environment, 23, 4021–4030(10).<br />

Preunkert, S., Wagenbach, D., Legrand, M., & Vincent, C. 2000. Col du Dome (Mont Blanc Massif,<br />

French Alps) suitability for ice core studies in relation with past atmospheric chemistry over Europe.<br />

Tellus, 52B, (3), 993–1012.


3.2. ICE AND CLIMATE 147<br />

Preunkert, S., Legrand, M., & Wagenbach, D. 2001. Sulfate trends in a Col du Dome (French Alps) ice<br />

core : A record of anthropogenic sulfate levels in the European midtroposphere over the twentieth<br />

century. Journal of Geophysical Research, 106, 31991–32004.<br />

Priscu, J., Adams, E., Lyons, W., Voytek, M., Mogk, D., Brown, R., McKay, C., Takacs, C., Welch,<br />

K., Wolf, C., Kirshtein, J., & Avci, R. 1999. Geomicrobiology of Subglacial Ice Above Lake Vostok,<br />

Antarctica.<br />

Raymond, C. F. 1983. Deformation in the vicinity of divides. Journal of Glaciology, 34, 357–373.<br />

Rohlfs, J. 2004. Zeitliche Variation von 10 Be in der Küstenantarktis - Eine Eiskernzeitreihe von<br />

Berkner Island. Diplomarbeit. <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg.<br />

Schock, M., Greilich, S., Wagenbach, D., Preunkert, S., Legrand, M., Petit, J. R., Flückiger, J.,<br />

Leuenberger, M., Haeberli, W., & Psenner, R. 2005. Dissolved organic carbon (DOC) in ice samples<br />

from non-temperated, polar and Alpine glaciers. Geophysical Research Abstracts, Vol. 7, 08671.<br />

Schöner, W., Auer, I., Böhm, R., Keck, L., & Wagenbach, D. 2002. Spatial representativity of air<br />

temperature information from instrumental and ice core based isotope records in the European<br />

Alps. Annals of Glaciology, 35, 157–161.<br />

Solanki, S. K., Usoskin, I. G., Kromer, B., Schüssler, M., & Beer, J. 2004. Unusual activity of the<br />

Sun during recent decades compared to the previous 11,000 years. Nature.<br />

Steier, P., Dellinger, F., Kutschera, W., Rom, W., & Wild, E. M. 2004. Pushing the precision limit<br />

of C14 measurements with AMS. Radiocarbon, 46, 969–978.<br />

Steier, P., Drosg, R., Kutschera, W., Wild, E. M., Fedi, M., Wagenbach, D., & Schock, M. 2005.<br />

Radiocarbon determination of particulate organic carbon (POC) in non-temperated, Alpine glacier<br />

ice (Abstract). The 10th International Conference on Accelerator Mass Spectrometry Berkeley,<br />

California, September 5-10, 2005.<br />

Wagenbach, D. 2004. Potential and restrictions of Alpine (mid-latitude) ice cores. Invited talk, SCIEM<br />

2000 (The synchronisation of civilization in the eastern Mediterranean in the 2nd Millenium BC)<br />

Workshop: Ashes and Ice, Vienna.<br />

Wagenbach, D., Ducroz, F., Mulvaney, R., Keck, L., Minikin, A., Legrand, M., Hall, J. S., & Wolff,<br />

E. W. 1998. Sea-salt aerosol in coastal Antarctic regions. Journal of Geophysical Research, 103(D9),<br />

10961–10974, 10.1029/97JD01804.<br />

Wegner, A. 2003. Die Geschichte der Sonnenaktivität im Antarktischen Eis Nachweis produktionsbedingter<br />

10 Be - Schwankungen. Diplomarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg.<br />

Wegner, A., Rohlfs, J., Huke, M., Stanzick, A., Wagenbach, D., Oerter, H., Sommer, S., Mulvaney,<br />

R., & Kubik, P. 2005. Bi-annual to decadal 10 Be variability in firn cores from Dronning Maud Land<br />

(DML) and Berkner Island (BI), Antarctica. Geophysical Research Abstracts, Vol 7, 08396.


Aquatic Systems<br />

4.1 Groundwater and Paleoclimate . . . . . . . . . . . . . . . . . . . . . . . . 151<br />

4.2 Lake Research (Limnophysics) . . . . . . . . . . . . . . . . . . . . . . . . 161<br />

149


4.1. GROUNDWATER AND PALEOCLIMATE 151<br />

Overview<br />

The research group ”Aquatic Systems” investigates freshwater systems, in particular lakes and groundwater,<br />

using direct measurements of physical parameters as wells as tracer and isotope methods. The<br />

fundamental goal of this research is to obtain a better understanding of the physical processes in these<br />

systems. Examples of studied processes are vertical turbulent mixing, currents, and tracer transport<br />

in stratified lakes, or recharge, flow, dispersion and contaminant transport in aquifers. A further important<br />

field is the use of aquifers as paleoclimate archives. The wider context of our research includes<br />

the issues of water resources protection and management, and assessment of past and present climate<br />

change.<br />

The group is divided in two subgroups: ”Groundwater and Paleoclimate” and ”Limnophysics”.<br />

4.1 Groundwater and Paleoclimate<br />

Names of group members<br />

Prof. Werner Aeschbach-Hertig, head of group<br />

Dr. Reinhold Bayer, administration<br />

Dr. Hany El-Gamal, PhD-student (completed June 2005)<br />

Dipl. Phys. Ronny Friedrich, PhD-student<br />

Dipl. Phys. Rainer Klement, diploma student (completed February 2005)<br />

Dipl. Phys. Tobias Kluge, PhD-student<br />

Dipl. Phys. Andreas Kreuzer, PhD-student<br />

Dr. Laszlo Palcsu, postdoc<br />

M. Sc. Sarah Rice, master student (completed December 2004)<br />

Dipl. Phys. Katja Träumner, diploma student (completed November 2005)<br />

Martin Wieser, diploma student<br />

Dipl. Ing. Gerhard Zimmek, technician<br />

Abstract The research group ”Groundwater and Paleoclimate” deals with applications of isotope<br />

and environmental tracers, in particular noble gases, in groundwater (and lakes in collaboration with<br />

the Limnophysics group). With theses methods, the group pursues two main aims: 1. To provide foundations<br />

for a sustainable management of groundwater resources, 2. Reconstruction of the paleoclimate<br />

since the last ice age.<br />

Background The overarching topic of our research may be summarized as ”isotope hydrology and<br />

climatology”, more specifically the use of isotopes and other environmental tracers (in particular noble<br />

gases) to study the functioning of groundwater systems and to extract paleoclimatic information from<br />

them.<br />

Isotope and tracer techniques have a long tradition in environmental physics. In addition to the widely<br />

used stable isotopes, dissolved noble gases in groundwater have been established as a reliable paleotemperature<br />

proxy. Furthermore, 3 H, He isotopes and other transient gas tracers are important tools<br />

in groundwater dating and recharge assessment [e.g. Kipfer et al. , 2002]. Groundwaters constitute<br />

by far the largest global reservoir of available fresh water. For the sustainable management of these<br />

resources, particularly in arid and semi-arid regions, it is essential to understand on what time-scales<br />

these resources are renewed and how they react to global climate change. Climate change and the<br />

limited availability of water resources are interrelated issues of increasing global importance. Isotopic<br />

studies of groundwaters yield information on both past climatic conditions such as temperature or<br />

aridity and on physical parameters such as residence time or recharge rate. Thus, issues of past climatic<br />

conditions and future availability of groundwater resources can be addressed in an integrated<br />

approach.<br />

Methods A central facility of the group is the newly built mass spectrometric system for the analysis<br />

of noble gases dissolved in water. It is currently becoming operational and will allow measurements<br />

of all stable noble gases from groundwaters for paleotemperature studies as well as the analysis of<br />

He isotopes for 3 H- 3 He dating. This facility is also being used to study new sample types such as<br />

stalagmites. It is complemented by an older system for He isotope analysis and a radiometric 3 H<br />

lab. Furthermore, the group conducts gas chromatographic SF6 analyses in cooperation with the<br />

limnophysics group, and uses the stable isotope and 14 C laboratories of the institute.


152 CHAPTER 4. AQUATIC SYSTEMS<br />

Main activities Projects of the group are related either to questions of water resources or paleoclimate,<br />

or both. Some projects are mainly applications of established methods, whereas others intend<br />

to develop new methods and approaches.<br />

The main goal of a project studying groundwater in the North China Plain is to obtain a noble gas<br />

paleotemperature record from a formerly little studied part of the world (see section 4.1.1). However,<br />

it also involves an investigation of the current recharge to the heavily exploited groundwater resources<br />

of this semi-arid area. Preliminary results of this study showing a clear paleoclimatic signal are being<br />

published in the framework of the IAEA isotope hydrology series [Kreuzer et al. , in press 2005].<br />

Similarly, a project on groundwater in Egypt focusses on the renewal rate of these resources that are<br />

used to sustain new agricultural developments outside the Nile Delta (see section 4.1.2). The study<br />

clearly shows that the regional groundwater originates from the Nile water, but the renewal is very<br />

slow. This project has been a cornerstone of the thesis of Hany El-Gamal [El-Gamal, 2005]. A paper<br />

is in preparation.<br />

Recharge rates and processes are also central to a project focussing on groundwater in the nearby<br />

Odenwald region (see section 4.1.3). However, the main problem in this case is not the overexploitation<br />

of the resource but the incomplete understanding of the connection between recharge in the mountains<br />

and water levels in the valley, where large water works are operating. Progress in this project has<br />

been and will again be reported at meetings of the hydrogeology section of the German Geological<br />

Society [Friedrich et al. , 2004].<br />

A new idea is to try and use microscopic water inclusions in speleothems (stalagmites and other<br />

carbonate sinters) to extract noble gas concentrations and temperatures (see section 4.1.4). After<br />

some preliminary studies in the form of diploma theses [Rice, 2004; Träumner, 2005], this issue is now<br />

studied in the framework of a DFG research unit in collaboration with the Radiometry Group of the<br />

”Heidelberger Akademie der Wissenschaften” (see section 5.1.8). The issue of the analysis of noble<br />

gases on very small samples and in new archives is also central to the project of our Marie Curie<br />

fellow Laszlo Palcsu (see section 4.1.5). However, the scope of this project is wider, trying to advance<br />

our general understanding of the ways in which noble gases in different archives can help us to gain<br />

paleoclimatic information.<br />

Another area of research that is currently developed is the study of interactions between groundwater<br />

and lakes, where a strong link between the two subgroups of the aquatic systems section becomes<br />

apparent (see section 4.1.6). A just completed diploma thesis investigated and validated the use of<br />

Radon as a tracer to study this interaction [Kluge, 2005].<br />

Funding The China project is funded by the DFG and its Chinese counterpart NSFC. The speleothem<br />

project is part of a DFG research unit (”Dated speleothems as archives of the paleo-environment”).<br />

The Odenwald project is a collaboration with the ”Hessisches Landesamt <strong>für</strong> Umwelt und Geologie”<br />

and the tracer analyses are funded by the State of Hessen. Hany El-Gamal was supported by a longterm<br />

mission fellowship of the Egyptian government. Laszlo Palcsu is supported by a Marie Curie<br />

EIF fellowship of the EU (project ”ADNOGAPALIN”).<br />

Cooperations In the above mentioned projects we cooperate with other groups of the institute,<br />

in particular with the carbon cycle group for stable isotope analyses on groundwaters and with the<br />

radiometry group for the preparation of 14 C samples for AMS analysis as well as on the study of<br />

fluid inclusions in speleothems. There exists also a cooperation with the ice and climate group on<br />

the analysis of He isotopes in ice. Cooperations outside the institute include local project partners<br />

in China, Egypt and Hessen. Furthermore, close links exist to the noble gas and AMS labs at ETH<br />

Zurich, where some of our samples are analysed, as well as to the isotope hydrology group at the<br />

University of Bern. Several links exist to scientists at the UFZ in Leipzig and Halle, and many new<br />

national and international cooperations will be forged in the framework of the upcoming DFG research<br />

unit.<br />

The institutions of our main cooperation partners are listed in the following (with shortcuts as used<br />

for author affiliations in the project reports):<br />

<strong>Institut</strong>e of Hydrogeology and Environmental Geology, Chinese academy of geological sciences, Zhengding,<br />

China (IHEG),<br />

Geology Department, Faculty of Science, Minufiya University, Shebin El-Kom, Egypt (MINUF),<br />

Hessisches Landesamt <strong>für</strong> Umwelt und Geologie, Wiesbaden, Germany (HLUG),<br />

<strong>Institut</strong> <strong>für</strong> Isotopengeologie und Mineralische Rohstoffe, ETH Zürich, Switzerland (ETHZ).


4.1. GROUNDWATER AND PALEOCLIMATE 153<br />

Publications<br />

Peer reviewed<br />

1. Aeschbach-Hertig [2005a]<br />

2. Corcho Alvarado et al. [2004]<br />

3. Peeters et al. [2004]<br />

Other publications<br />

1. Kreuzer et al. [in press 2005]<br />

Doctoral theses<br />

1. El-Gamal [2005]<br />

Diploma theses<br />

1. Klement [2005]<br />

2. Kluge [2005]<br />

3. Rice [2004]<br />

4. Träumner [2005]<br />

Invited Talks<br />

1. Aeschbach-Hertig [2005b]<br />

2. Aeschbach-Hertig [2004c]<br />

3. Aeschbach-Hertig [2004a]<br />

4. Aeschbach-Hertig [2004d]<br />

5. Aeschbach-Hertig [2004b]


154 CHAPTER 4. AQUATIC SYSTEMS<br />

4.1.1 A tracer study of paleoclimate and groundwater recharge in the<br />

North China Plain<br />

Participating scientists Andreas M. Kreuzer, Christoph v. Rohden, Werner Aeschbach-Hertig,<br />

Chen Zongyu (IHEG), Rolf Kipfer (ETHZ)<br />

Abstract Noble gas temperatures (NGTs), stable isotope ratios and 14 C-ages from old groundwater<br />

in the North China Plain (NCP) are used to reconstruct a paleoclimate record. This is the first NGT<br />

record from East Asia. Preliminary results indicate a glacial cooling of about 4 ◦ C .<br />

NGT (°C)<br />

15.5<br />

15.0<br />

14.5<br />

14.0<br />

13.5<br />

13.0<br />

12.5<br />

12.0<br />

11.5<br />

11.0<br />

10.5<br />

10.0<br />

9.5<br />

9.0<br />

8.5<br />

8.0<br />

7.5<br />

2.6<br />

Noble Gas Temperatures of different wells<br />

Avg. 12.8°C<br />

7<br />

15.5<br />

13<br />

10<br />

12<br />

0 50 100 150 200 250 300 350 400<br />

12<br />

18<br />

11<br />

Avg. 9.0°C<br />

Approx. distance from well #1 (km)<br />

Numbers below points<br />

indicate age of<br />

specific well in ka.<br />

(Data from Zongyu, 2003)<br />

Figure 4.1: The figure shows the noble gas temperatures for the samples from 2004. There are warm temperatures<br />

of about 13 ◦ C in the infiltration area (on the left end), which correspond to the local annual air temperatures. The<br />

transition from the holocene to the last glacial occurs at about 100 km from well no.1 accompanied by a clear signal in<br />

temperature.<br />

Background Noble gas concentrations in water<br />

vary with temperature as the solubilities are temperature<br />

dependent. Measurements of noble gases<br />

in paleo-groundwater can therefore be used to calculate<br />

paleo-recharge temperatures [Kipfer et al.<br />

, 2002]. The importance of this method lies in<br />

reliable determination of glacial-interglacial temperature<br />

differences. The age of the groundwater<br />

in the NCP reaches from very young water to<br />

20 kyr old water in the deeper parts of the aquifers<br />

[Zongyu et al. , 2003].<br />

The goal of this study is to complement isotope<br />

data from this aquifer system with NGTs in order<br />

to quantify the climatic signal of the transition<br />

from the last glacial maximum (LGM) to the<br />

holocene.<br />

Methods and results Last years measurements<br />

showed a clear temperature signal at about<br />

100 km from well #1 as shown in the figure. This<br />

year a second sampling campaign was conducted<br />

in April to sample a short distance where the transition<br />

from the last glacial to the holocene was<br />

expected.<br />

A clear climatic signal is also present in the sta-<br />

ble isotope data corroborating previous results of<br />

Zongyu et al. [2003].<br />

For radiocarbon dating of groundwater a new<br />

extraction-line was developed and built. A total<br />

amount of about 200ml of water is needed, which<br />

is then acidified under vacuum to release the dissolved<br />

inorganic carbon from the water. The carbon<br />

dioxide is then trapped in a special volume<br />

in liquid nitrogen and is further treated and prepared<br />

for accelerator mass spectrometry.<br />

Funding This work is financially supported by<br />

the DFG (DFG grant AE 93/1) and by the<br />

National Natural Science Foundation of China<br />

(NSFC grant No. 40472125)<br />

Outlook/Future work The dating with 14 C<br />

will be done by the end of this year and also the<br />

measurement of the new noble gas samples will be<br />

finished this year. It is planned to present the results<br />

at international conferences and to prepare<br />

publications.<br />

Main publication Kreuzer et al. [in press<br />

2005]


4.1. GROUNDWATER AND PALEOCLIMATE 155<br />

4.1.2 A multi-tracer study of groundwater in reclamation areas south-west<br />

of the Nile Delta, Egypt<br />

Participating scientists Werner Aeschbach-Hertig, Hany El-Gamal, Kamal Dahab (MINUF), Rolf<br />

Kipfer (ETHZ)<br />

Abstract The origin and renewal rate of groundwater used for irrigation in Egypt was investigated<br />

using a variety of isotope and tracer techniques ( 2 H, 18 O, 14 C, SF6, 3 H- 3 He, noble gases). The main<br />

result is that the groundwater is recharged from the Nile river, albeit at a slow rate. Water younger<br />

than 50 yr is found only in the vicinity of surface water features in the Nile Delta.<br />

� � ���per mil�<br />

20<br />

0<br />

-20<br />

-40<br />

-60<br />

-80<br />

GMWL<br />

A<br />

Paleowater<br />

Pre-1969 Nile water<br />

Precipitation<br />

-12 -10 -8 -6 -4 -2 0 2 4<br />

�<br />

� 18<br />

O [per mil]<br />

Figure 4.2: Mixing trend lines in stable isotope data. Squares A, B, and C indicate endmembers, dots<br />

represent precipitation data, and triangles represent data from the wells. The latter lie on mixing lines<br />

(dashed) between regional paleogroundwater and Nile water from before and after the completion of<br />

the Aswan High Dam in 1969. These data clearly show that the groundwater is mainly recharged<br />

from the surface water, but at a slow rate, such that most of the water infiltrated before 1969.<br />

Background Egypt develops new agricultural<br />

areas outside the overpopulated Nile Delta and<br />

Valley. Such so-called reclamation areas depend<br />

almost exclusively on groundwater as water resource.<br />

For the long-term sustainability of these<br />

developments it is of central importance to understand<br />

the processes and rates of recharge of the<br />

groundwater resources.<br />

Methods and results The transient environmental<br />

tracers SF6 and 3 H- 3 He have been used<br />

to date the shallow groundwater, whereas dating<br />

of the old groundwater by 14 C is currently<br />

in progress. Noble gases and stable isotopes have<br />

been analysed to obtain information on the conditions<br />

during recharge. The results of the SF6<br />

and 3 H- 3 He dating show that only the wells that<br />

are located within a few kilometers of the artificial<br />

irrigation canals in the delta have young ages of<br />

between 1 and 25 years, indicating direct recharge<br />

by water derived from the river. At larger distance<br />

from the surface water, the age of the groundwater<br />

exceeds the detection limit of these methods<br />

B<br />

C<br />

Recent<br />

Nile<br />

water<br />

(30 - 50 yr). The 14 C-analyses will provide information<br />

on the age of the groundwater in the<br />

reclamation areas, some tens of kilometers apart<br />

from the surface water. The stable isotope data<br />

provide clear indications of the on origin and age<br />

of the groundwater, due to the change (enrichment<br />

by evaporation) of the isotopic signature of<br />

the Nile water resulting from the construction of<br />

the Aswan High Dam in 1969 (see figure). Only<br />

groundwater samples from the vicinity of the river<br />

lie close to the the recent Nile water composition.<br />

Most of the data lie close to the former Nile composition<br />

but not the local precipitation, indicating<br />

paleo-recharge derived from the river.<br />

Outlook/Future work The 14 C ages should<br />

enable us to further constrain the renewal rate<br />

of the groundwater and thus to contribute crucial<br />

information for a sustainable management of this<br />

resource. A publication is in preparation.<br />

Main publication El-Gamal [2005]


156 CHAPTER 4. AQUATIC SYSTEMS<br />

4.1.3 A multi tracer study to investigate the groundwater in the Odenwald<br />

region<br />

Participating scientists Ronny Friedrich, Werner Aeschbach-Hertig, Bernhard Leßmann (HLUG),<br />

Guido Vero (HLUG)<br />

Abstract Three sampling campaigns where performed during 2003, 2004 and 2005 in the Odenwald<br />

region. With this multi tracer study (noble gases, 3 H, δ 18 O, δ 2 H, SF6, CFCs) we want to investigate<br />

the age structure, mixing ratios and recharge areas of the groundwater in this region. First results<br />

show groundwater ages of a few years up to older than 40 years.<br />

Figure 4.3: Stable isotope data (δ 18 O, δ 2 H) of the campaign in 2003. Isotopic signatures of samples<br />

from the crystalline part (1), the sandstone part (2) and from the ”Hanau-Seeligenstädter-Senke” (4)<br />

are concentrated in separate groups, whereas samples from ”Hessisches Ried” (3) scatter over the<br />

whole range.<br />

Background The Odenwald region is one of<br />

the main recharge areas for groundwater of<br />

the surrounding areas (Hessisches Ried, Hanau-<br />

Seligenstädter Senke). These areas are very important<br />

for freshwater extraction. Therefore we<br />

want to investigate the groundwater in the Odenwald<br />

to study residence times and mixing ratios<br />

of the groundwater, define regions of groundwater<br />

recharge and understand the groundwater inflow<br />

from the Odenwald to the surrounding areas.<br />

Funding This work is done in cooperation with<br />

the ”Hessisches Landesamt <strong>für</strong> Umwelt und Geologie”<br />

Wiesbaden.<br />

Methods and results To study the groundwater<br />

we use different stable and radioactive gasand<br />

isotope tracers summarized as ”environmental<br />

tracers” such as 2 H, 18 O, 3 H, noble gases and<br />

SF6. Noble gases (He, Ne, Ar, Kr, Xe) can be<br />

used in principle to calculate recharge temperatures<br />

or the infiltration altitudes (above sea level)<br />

of recharge areas. Furthermore noble gases give<br />

important information to correct other gas tracers<br />

for so called ”excess air” that oversaturates<br />

gases in groundwater (see Kipfer et al. [2002] for<br />

a review of the methods). SF6 and 3 H- 3 He are<br />

used to date the groundwater.<br />

Comparing the results of these two independent<br />

dating methods we see that dating with SF6 is not<br />

possible in the crystalline region of the Odenwald.<br />

We assume that SF6 is influenced by a natural<br />

source in the subsurface. Data from the 3 H- 3 He<br />

method give robust groundwater ages in the range<br />

of some years to values higher than 40 years. By<br />

using the stable isotope data it is possible to distinguish<br />

between groundwater from different areas<br />

of the Odenwald. That will help us to define flow<br />

paths of the groundwater from the Odenwald to<br />

the surrounding areas. Additionally the isotopic<br />

signatures show that the groundwater was formed<br />

by ”annual” precipitation and not only in winteror<br />

summertime.<br />

Outlook/Future work Until today we have<br />

analyzed all samples from the campaign in 2003.<br />

Measuring the samples from 2004 and 2005 should<br />

give us information about seasonal changes in<br />

groundwater flow.<br />

Main publication Friedrich et al. [2004]


4.1. GROUNDWATER AND PALEOCLIMATE 157<br />

4.1.4 A new mass spectrometric system for measurement of noble gases<br />

and first applications to perform measurements of fluid inclusions in<br />

speleothems<br />

Participating scientists Katja Träumner, Werner Aeschbach-Hertig, Ronny Friedrich, Laszlo Palcsu<br />

and Gerhard Zimmek<br />

Abstract A new mass spectrometric system for purification and measurement of noble gases from<br />

groundwater and stalagmite samples was put into operation and tested for its behavior. The first<br />

application was a successful testing of a new extraction method for stalagmite samples.<br />

Desorption<br />

120%<br />

100%<br />

80%<br />

60%<br />

40%<br />

20%<br />

Desorption characteristic charcoal trap<br />

0%<br />

0 20 40 60 80 100 120 140<br />

-20%<br />

Temperature [K]<br />

Helium<br />

Neon<br />

Figure 4.4: The desorption of helium and neon from the charcoal trap as a function of temperature is<br />

shown. The decrease of the Helium-signal is a result of the gas consumption of the Quadrupol mass<br />

spectrometer which was used for measurement. On account of this characteristic curves a separation<br />

of helium and neon is possible, which is necessary for an exact measurement in the mass spectrometer.<br />

Background The characteristic temperature<br />

dependence of the solubility of noble gases and<br />

their property of being chemically and biologically<br />

inert, make noble gases an ideal proxy for<br />

paleotemperatures [Kipfer et al. , 2002]. By measuring<br />

noble gas concentrations of small fluid inclusions<br />

in stalagmite samples, we try to combine<br />

this thermometer with the possibility to precisely<br />

date the speleothem archive.<br />

Methods and results After first experiences<br />

with the extraction of fluid inclusions in the institute<br />

by a master thesis in the last year [Rice,<br />

2004], now the development of a new mass spectrometric<br />

system was the next step. This system<br />

consists of an inlet part to attach several kinds<br />

of samples, a system of cold traps for purification<br />

and separation (one trap cooled by dry ice<br />

for removal of water, one nude metal trap to condense<br />

all gases except helium and neon and a charcoal<br />

trap for separating helium and neon) and a<br />

commercial mass spectrometer, which is especially<br />

designed for measuring noble gases (see section<br />

4.1.5).<br />

During the diploma thesis the software to control<br />

all valves and to supervise the pressure in the line<br />

was written; software, tests and the parameters<br />

for temperature control of the traps were developed<br />

and several volumes (pipettes, standards, expansion<br />

and splitting volumes) of the system were<br />

determined. The new system was tested for the<br />

temporal behavior of the cool down processes and<br />

the desorption properties of the cold traps.<br />

The results of these tests were used to develop a<br />

new measurement routine. To continue the work<br />

with fluid inclusions in speleothems a new crushing<br />

method was tested. First measurements show<br />

that good results depend on the kind of samples.<br />

The composition of noble gases from stalagmites<br />

is a mixture of gases from air and from water.<br />

Outlook/Future work An automated measurement<br />

of samples will soon be possible. We<br />

will obtain a sample throughput of at least two to<br />

three samples a day. The work with the stalagmite<br />

samples will be continued by a Ph.D. thesis.<br />

Main publication Träumner [2005]


158 CHAPTER 4. AQUATIC SYSTEMS<br />

4.1.5 Advancing the use of noble gases as palaeoclimate indicators<br />

Participating scientists Laszlo Palcsu, Werner Aeschbach-Hertig<br />

Abstract A better understanding of gas partitioning during groundwater infiltration is a prerequisite<br />

for the reliable use of noble gases as palaeoclimate proxies. The primary goal of the present project<br />

is to obtain a detailed understanding of the physical mechanisms linking climate and soil parameters<br />

to the noble gas patterns imprinted during groundwater recharge.<br />

Figure 4.5: Results of stability tests of the new noble gas system, showing the deviation of different<br />

noble gas measurements from the average (X-axis: number of measurements, Y-axis: deviation in %).<br />

Background The analysis of dissolved noble<br />

gas concentrations in groundwater has proven to<br />

be a reliable method to determine quantitative<br />

palaeotemperatures [Kipfer et al. , 2002]. Noble<br />

gas studies in semi-arid regions have shown that<br />

in addition to recharge temperatures, the ”excess<br />

air” phenomenon may be useful as a proxy for<br />

the important climate parameter humidity [Beyerle<br />

et al. , 2003]. The present project aims at<br />

advancing and broadening the scope and applicability<br />

of noble gases in palaeoclimatology and hydrology,<br />

in particular at establishing the palaeoclimatic<br />

significance of excess air. This objective<br />

shall be achieved by careful analysis of noble gas,<br />

climate, and soil data from several semi-arid regions,<br />

complemented by experiments on the scale<br />

of laboratory soil columns and test-fields.<br />

Methods and results To interpret the dissolved<br />

noble gases in water as noble gas temperature<br />

and excess air component with low error it is<br />

necessary to achieve a very precise measurement<br />

of noble gases. Therefore, the accuracy of each<br />

noble gas measurement should be around 1 % or<br />

better. Noble gas measurents are performed by a<br />

new GV 5400 noble gas mass spectrometer which<br />

was purchased and installed in 2004. The GV<br />

5400 is an all-metal, statically operated, double focused,<br />

90 ◦ sector field mass spectrometer with 57<br />

cm extended geometry. So far, sensitivities and reproducibilities<br />

were determined. According to the<br />

acceptance specification, the achieved sensitivities<br />

are 7.52·10 −4 Amps/Torr for 40 Ar, and 3.47·10 −4<br />

Amps/Torr for 4 He, respectively. Stability and<br />

reproducibility measurements were performed on<br />

normal air samples. An individual sample could<br />

be measured within a few permil relative error,<br />

while the results of several measurements differed<br />

from each other by 1-2 %. The standard deviation<br />

of the 4 He and 3 He measurement were 0.6 %<br />

and 1.2 %, whilst the measured data were varying<br />

within the range of ±1 % and ±3 % around the<br />

average (see Figure). The standard deviation of<br />

the heavier noble gases were 0.3 % for neon, 0.5 %<br />

for argon, 1.0 % for krypton, and 0.9 % for xenon.<br />

These accuracies allow us to determine noble gas<br />

temperatures with an error of about 0.5 ◦ C and<br />

very precise excess air components.<br />

Outlook/Future work Laboratory and field<br />

experiments will be started in the next months<br />

in order to investigate the mechanisms which are<br />

responsible for the excess air formation. Furthermore,<br />

using the ability for precise noble gas measurements,<br />

the potential of fluid inclusions in stalagmites<br />

and other carbonate deposits from caves<br />

as palaeoclimate archives will also be investigated<br />

(see section 4.1.4).<br />

Funding This project is supported by the Marie<br />

Curie Intra-European Fellowships program (reference<br />

number: 009562).


4.1. GROUNDWATER AND PALEOCLIMATE 159<br />

4.1.6 Radon as tracer for lake - groundwater interaction<br />

Participating scientists Tobias Kluge, Werner Aeschbach-Hertig, Christoph v. Rohden, Johann<br />

Ilmberger<br />

Abstract Using the radioactive noble gas radon-222, the groundwater inflow into a lake is calculated<br />

from vertical profiles. With the aid of a newly developed sensitive technique, a clear groundwater signal<br />

has been detected in the lake.<br />

depth (m)<br />

0<br />

5<br />

10<br />

15<br />

epilimnion<br />

thermocline<br />

hypolimnion<br />

typ. error<br />

0 5 10 15 20 25 30<br />

Bq/m 3<br />

20.June<br />

4.July<br />

12.July<br />

19.July<br />

26.July<br />

Figure 4.6: Vertical radon profile in Lake Willersinnweiher, a lake with significant groundwater inflow<br />

in the upper part. This inflow produces a radon maximum in the thermocline. In the epilimnion,<br />

outgassing into the atmosphere reduces the radon activity.<br />

Background In this study we investigated the<br />

lake - groundwater interaction at a lake in the<br />

Rhine-Valley without surface inflow from rivers.<br />

One focus was to quantify the groundwater inflow.<br />

This inflow is used to calculate the replacement<br />

time of the lake water, which is of great ecological<br />

and hydrological significance.<br />

Rn-222 is a suitable tool to detect even a very<br />

small amount of groundwater inflow, because the<br />

activity difference between groundwater and lake<br />

- or surface water is very high. In the study area<br />

the activity concentration of radon in the groundwater<br />

is between 5 000 and 10 000 Bq/m 3 and in<br />

the lake water it is < 50 Bq/m 3 .<br />

Methods and results The measurements are<br />

done with an alpha-spectrometer (RAD7). This<br />

spectrometer detects the decay products of radon<br />

in the gas phase. To evaluate the radon activity<br />

of water, radon in sample water is brought into<br />

equilibrium with radon in a closed air loop. The<br />

activity in the air loop is only controlled by the<br />

amount of radon in water and its solubility. A new<br />

technique with large (12 l) water samples was de-<br />

veloped to reduce the detection limit.<br />

To explain the results, the sources of radon have<br />

to be known. The first possibility is the dissolved<br />

radium, that can decay directly into radon. Another<br />

source is the emanation from the lake sediments<br />

and the inflow of dissolved radon with the<br />

groundwater. Loss is caused by decay and outgassing<br />

into the atmosphere. The vertical profile<br />

can only be explained by a strong groundwater<br />

inflow in the epilimnion and a negligible inflow in<br />

the hypolimnion.<br />

By dividing the lake in different boxes according<br />

to the structure of stratification, a water balance<br />

was calculated. The replacement time for the epilimnion<br />

is (4.7 ± 1.2) years, for the hypolimnion<br />

ca. 21 years. In addition to previous studies,<br />

statements about depth-dependent groundwater<br />

inflow are possible. Due to the large number of<br />

constraints an exact calculation of the smallest<br />

and greatest possible groundwater inflow can be<br />

made.<br />

Main publication Kluge [2005]


160 CHAPTER 4. AQUATIC SYSTEMS<br />

References<br />

Aeschbach-Hertig, W. 2004a. Climate of the Past as a Basis for an Assessment of the Future. Invited<br />

talk, GSI-Kolloquium, Darmstadt, Germany.<br />

Aeschbach-Hertig, W. 2004b. Environmental Tracers in Groundwater Studies - Water Resources and<br />

Paleoclimate. Invited talk, <strong>Institut</strong>e of Hydrogeology and Environmental Geology, Chinese Academy<br />

of Geological Sciences, Zhengding, China.<br />

Aeschbach-Hertig, W. 2004c. Excess Air in Groundwater: Problems and Opportunities. Invited<br />

keynote presentation, Annual Meeting of the Geological Society of America (GSA), Denver, USA.<br />

Aeschbach-Hertig, W. 2004d. Noble Gases and Excess Air in Groundwater: Review and Outlook.<br />

Invited talk, KUP-Seminar, University of Bern, Switzerland.<br />

Aeschbach-Hertig, W. 2005a. A comment on ”Helium sources in passive margin aquifers-new evidence<br />

for a significant mantle 3 He source in aquifers with unexpectedly low in situ 3 He/ 4 He production”<br />

by M. C. Castro [Earth Planet. Sci. Lett. 222 (2004) 897-913]. Earth Planet. Sci. Lett., in press.<br />

Aeschbach-Hertig, W. 2005b. Surface and Subsurface Waters. Invited lecture, WE-Heraeus summerschool<br />

”Physics of the Environment”, Bad Honnef, Germany.<br />

Beyerle, U., Rüedi, J., Leuenberger, M., Aeschbach-Hertig, W., Peeters, F., Kipfer, R., & Dodo, A.<br />

2003. Evidence for periods of wetter and cooler climate in the Sahel between 6 and 40 kyr BP<br />

derived from groundwater. Geophys. Res. Lett., 30(4), 1173, doi:10.1029/2002GL016310.<br />

Corcho Alvarado, J. A., Purtschert, R., Hinsby, K., Troldborg, L., Hofer, M., Kipfer, R., Aeschbach-<br />

Hertig, W., & Synal, H.-A. 2004. 36 Cl in modern groundwater dated by a multi tracer approach<br />

( 3 H/ 3 He, SF6, CFC-12 and 85 Kr): A case study in quaternary sand aquifers in the Odense Pilot<br />

River Basin, Denmark. Appl. Geochem., 20, 599–609.<br />

El-Gamal, H. 2005. Environmental tracers in groundwater as tools to study hydrological questions in<br />

arid regions. PhD thesis, University of Heidelberg.<br />

Friedrich, R., Aeschbach-Hertig, W., Vero, G., & Leßmann, B. 2004. Einsatz von Umwelttracern zur<br />

Erkundung des Grundwassers der Odenwald-Region. Page 35 of: Schiedek, T., Kaufmann-Knoke,<br />

R., & Ebhardt, G. (eds), Hydrogeologie regionaler Aquifersysteme (FH-DGG-Tagung). Schriftenreihe<br />

der Deutschen Geologischen Gesellschaft, vol. 32. Darmstadt: Deutsche Geologische Gesellschaft.<br />

Kipfer, R., Aeschbach-Hertig, W., Peeters, F., & Stute, M. 2002. Noble gases in lakes and ground waters.<br />

Pages 615–700 of: Porcelli, D., Ballentine, C., & Wieler, R. (eds), Noble gases in geochemistry<br />

and cosmochemistry. Rev. Mineral. Geochem., vol. 47. Washington, DC: Mineralogical Society of<br />

America, Geochemical Society.<br />

Klement, R. 2005. Optimierung von SF6-Grundwasserprobenahme-Methoden. Diplomarbeit, <strong>Universität</strong><br />

Heidelberg.<br />

Kluge, T. 2005. Radon als Tracer in aquatischen Systemen. Diplomarbeit, <strong>Universität</strong> Heidelberg.<br />

Kreuzer, A. M., Zongyu, C., Kipfer, R., & Aeschbach-Hertig, W. in press 2005. Environmental Tracers<br />

in Groundwater of the North China Plain. In: IAEA (ed), International Conference on Isotopes in<br />

Environmental Studies - Aquatic Forum 2004. Monte-Carlo, Monaco: IAEA.<br />

Peeters, F., Beyerle, U., Aeschbach-Hertig, W., Brennwald, M. S., & Kipfer, R. 2004. Response to<br />

the comment by G. Favreau, A. Guero, and J. Seidel on Improving noble gas based paleoclimate<br />

reconstruction and groundwater dating using 20 Ne/ 22 Ne ratios (2003) Geochim. Cosmochim. Acta,<br />

67, 587 - 600. Geochim. Cosmochim. Acta, 68(6), 1437–1438.<br />

Rice, S. 2004. The development of a method for the extraction and measurement of noble gases from<br />

fluid inclusions in samples of calcium carbonate. Master thesis, University of Heidelberg.<br />

Träumner, K. 2005. Inbetriebnahme, Tests und erste Anwendung einer neuen Aufbereitungslinie zur<br />

massenspektrometrischen Messung von Edelgasen aus Grundwasser - und Stalagmitproben. Diplomarbeit,<br />

<strong>Universität</strong> Heidelberg.<br />

Zongyu, C., Jixiang, Q., Jianming, X., Jiaming, X., Hao, Y., & Yunju, N. 2003. Paleoclimatic<br />

interpretation of the past 30 ka from isotopic studies of the deep confined aquifer of the North<br />

China plain. Appl. Geochem., 18, 997–1009.


4.2. LAKE RESEARCH (LIMNOPHYSICS) 161<br />

4.2 Lake Research (Limnophysics)<br />

Names of group members<br />

Dr. Johann Ilmberger, head of group<br />

Dr. Christoph von Rohden, postdoc<br />

Dipl. Phys. Karl Wunderle, diploma student (completed April 2005)<br />

Abstract Water quality of lake waters is, among other factors, affected by mixing and transport<br />

processes in the interior, as well as by the exchange with the ambient ground water. These internal<br />

processes and the ground water exchange are the main subjects of our investigations.<br />

Figure 4.7: Schematic diagramm of transport processes in lakes.<br />

Background Transport processes in lakes are important for the lake water quality. Especially<br />

mining lakes tend to have a poor quality because of the disturbed landscape due to the mining<br />

activities.<br />

Methods The investigations are based on tracers and direct measurements. Mainly we are using<br />

the tracer SF6, but also stable isotopes and now upcoming Radon (see section 4.1.6).<br />

The background level of SF6 can be used to study the interaction of ground water with lake water.<br />

This is based on the equilibration of rain and surface waters with atmospheric gases and the increase<br />

of the atmospheric level of the man made SF6 during the last decades. Therefore ground water -as it<br />

normally infiltrated a few decades ago- has a low SF6 content, while the lake water SF6 concentration<br />

is, at least during overturn, close to the (higher) atmospheric concentration. This difference of the<br />

signals can be used to study ground water - lake water exchange. We will try to apply this method<br />

to the mining lake RL117.<br />

We use SF6 spike experiments to investigate vertical mixing and ground water exchange. There we<br />

inject a small amount SF6 (few hundred mg) into the (hypolimnic) water body and trace the vertical<br />

spread and the balance by profile measurements (see section 4.2.1). We applied this method to Lake<br />

Constance, Lake Hufeisensee, Lake Merseburg Ost 1a and 1b. We will apply it at Lake Waldsee.<br />

Direct measurements include the profile measurements of temperature and electrical conductivity with<br />

a CTD-probe at a vertical resolution of ∼2cm (see section 4.2.2), continuous temperature measurements<br />

at different water depths using logging temperature probes and measurements of water currents<br />

with an Acoustic Doppler Current Profiler (see section 4.2.3).<br />

Lakes in investigation: Mining lake Merseburg Ost 1a, Mining lake Merseburg Ost 1b, Lake Willersinnweiher,<br />

Lake Waldsee, Lake RL117.<br />

The tracer methods, especially the spike experiments, are very well suited for the transport investigations.<br />

Projects and funding<br />

Our work at Willersinnweiher, where we did current measurements, continuous temperature and CTD-


162 CHAPTER 4. AQUATIC SYSTEMS<br />

profile measurements, was funded by the SFB 359: ”Reaktive Strömungen, Diffusion und Transport”,<br />

Teilprojekt D2 (see section 4.2.3).<br />

The SF6 spike measurements at the mining lakes Merseburg 1a and 1b were funded by the Centre<br />

of Environmental Research Leipzig-Halle and performed in close collaboration with B. Böhrer (UFZ-<br />

Leipzig/Halle, Section Gewässerforschung, Magdeburg).<br />

In the future we will intensify the research using radon as limnic tracer, as the work of Tobias Kluge<br />

has shown its potential as tracer for the groundwater exchange of gravel lakes (see section 4.1.6).<br />

In a joined project, funded by the German Research Foundation, we will investigate vertical transport<br />

and groundwater exchange at two mining lakes (Lake Waldsee and Lake RL117).<br />

Collaborations<br />

UFZ Leipzig-Halle, Dept. of Lake Research Magdeburg and Dept. of Isotope Hydrology<br />

BTU Cottbus, Lehrstuhl Gewässerschutz<br />

<strong>Institut</strong>e for Biodiversity and Ecosystem Dynamics / Aquatic Microbiology, University of Amsterdam<br />

Limnologisches <strong>Institut</strong>, <strong>Universität</strong> Konstanz<br />

<strong>Institut</strong> <strong>für</strong> Seenforschung, Langenargen, LfU<br />

Publications<br />

Other publications<br />

1. Ilmberger & von Rohden [2005]<br />

2. Ilmberger et al. [2005]<br />

3. von Rohden et al. [2005]<br />

Diploma theses<br />

1. Wunderle [2005]


4.2. LAKE RESEARCH (LIMNOPHYSICS) 163<br />

4.2.1 Sulfurhexaflourid (SF6) as tracer for transport and mixing processes<br />

in mining lakes<br />

Participating scientists Johann Ilmberger, Christoph von Rohden<br />

Abstract To study transport and mixing processes in the monimolimnion of mining lakes we released<br />

a small quantity of the trace gas in the monimolimnion of two mining lakes. The vertical spread and<br />

the mass balance were used to gain information about the vertical diffusion and the ground water<br />

exchange.<br />

Figure 4.8: SF6 - quantity in the monimolimnion (the water mass below 56.55 m asl) of the mining<br />

lake Merseburg-Ost 1a versus time. The experiment was started in 1997 and today we still can balance<br />

the trace gas by measuring a vertical profile. The SF6 decreases at a rate of 0.12 yr −1 , which is mainly<br />

due to ground water exchange.<br />

Background Because of their geometry, which<br />

is the result of the mining activities, mining lakes<br />

tend to have a water body which is not involved<br />

in the yearly cycle of mixing, a monimolimnion.<br />

These monimolimnia usually have a very poor water<br />

quality and might be enriched by heavy metals<br />

and other toxicities. Therefore one would like to<br />

know how persistent they are, or how high the<br />

risk is to contaminate the lake water and/or the<br />

ambient ground water.<br />

Funding This work was funded by the Centre<br />

of Environmental Research Leipzig-Halle.<br />

Methods and results The man made and industrially<br />

used gas sulfur hexaflouride (SF6) is<br />

very well suited to trace transport processes in<br />

strongly stratified waters, because it is chemically<br />

inert much as a noble gas. So far no other than<br />

the (very slow) degradation in the higher atmosphere<br />

is reported. And, because of its high electronegativity,<br />

it can be detectet very sensitively<br />

by an ECD detector after separation by gas chromatography.<br />

Our detection limit is ∼ 10 −17 Mol<br />

(10 aMol). For comparison: water, in equilibrium<br />

with the modern atmosphere ( 6 pptv), has a concentration<br />

of 2 fMol/l (= 2 · 10 −15 Mol/l). In<br />

1997 we started a tracer experiment in the monimolimnion<br />

of the open pit mining lake Merseburg-<br />

Ost 1a [von Rohden & Ilmberger, 2001]. To investigate<br />

the transport processes we injected 0.1<br />

mMol (15 mg) of SF6 into the interior of the monimolimnion.<br />

The monimolimnion has a salinity of<br />

about 40�, is about 2 m high and within a distance<br />

of 20 cm it changes to the hypolimnic salinity<br />

of 4�. The figure shows the total SF6 content<br />

of the monimolimnion calculated from profiles<br />

sampled at a vertical distance of 20 cm. The<br />

SF6 content of the monimolimnion changed from<br />

the initial 100 Mol down to 45 Mol at the beginning<br />

of 2004. A logarithmic fit to the values<br />

leads to a loss rate of 0.12 yr −1 . So 12% of the<br />

content leaves the monimolimnion per year. As<br />

we find only very little SF6 escaping into the hypolimnion<br />

and even a decrease in concentration<br />

directly above the lake floor, the loss is mainly<br />

due to ground water exchange.<br />

Outlook/Future work Though we do not<br />

have further funding for this research we will try<br />

to continue these very interesting investigations.<br />

Main publication Ilmberger & von Rohden<br />

[2005]


164 CHAPTER 4. AQUATIC SYSTEMS<br />

4.2.2 Vertical transport in stratified lakes<br />

Participating scientists Christoph von Rohden<br />

Abstract Based on measurements of the environmental tracers temperature and sulfur hexafluoride,<br />

effective vertical exchange coefficients Kz in density stratified lakes were calculated using budget<br />

methods. The heat transport in summer stratification can be limited to conduction. Molecular<br />

diffusion was found to be the only exchange process in lakes with strong chemical stratification.<br />

height [m asl]<br />

88<br />

86<br />

84<br />

s u r f a c e<br />

82<br />

80<br />

78<br />

76<br />

74<br />

72<br />

70<br />

68<br />

5 10 15 20 25 10 -5<br />

10 -4<br />

10 -3<br />

2004<br />

t h e r m o c l i n e<br />

05.11.<br />

22.10.<br />

24.09.<br />

14.09.<br />

03.09.<br />

25.08.<br />

10.08.<br />

30.07.<br />

16.07.<br />

06.07.<br />

25.06.<br />

07.06.<br />

08.06.<br />

27.05.<br />

a)<br />

17.05.<br />

07.05.<br />

b o t t o m<br />

b)<br />

temperature [°C]<br />

stratification stability N 2 [s -1 stability N<br />

]<br />

2<br />

10 -2<br />

heat conduction<br />

10 -7<br />

10 -6<br />

c)<br />

10 -5<br />

diffusion coefficient K z [m 2 /s]<br />

Figure 4.9: a) Temperature profiles during the summer stratification, b) mean stability (acting against<br />

vertical exchange) due to temperature gradients, c) calculated parameter Kz (average) representing<br />

the intensity of exchange.<br />

Background In density stratified lakes, the extent<br />

of the redistribution of geochemically relevant<br />

species caused by the wind driven internal<br />

dynamics is of interest. On time scales of weeks<br />

to months, the vertical transport during stratification<br />

is a result of small scale turbulent motions.<br />

It can be quantified by calculating Kz as effective<br />

vertical exchange coefficients.<br />

Funding The work was supported by the SFB<br />

359 “Reaktive Strömungen, Diffusion und Transport”,<br />

University of Heidelberg and the Centre<br />

for Environmental Research (UFZ) Leipzig-Halle,<br />

Department of Lake Research, Magdeburg.<br />

Methods and results The investigations are<br />

based on high resolution profiles of temperature<br />

and conductivity (taken with an automatic probe)<br />

and gas chromatographic measurements of the artificial<br />

tracer sulfur hexafluoride. Assuming horizontal<br />

homogeneity, which is reasonable in small<br />

lakes, the experimental setup was one dimensional<br />

taking into account the morphology of the lakes.<br />

The transport intensity was quantitatively estimated<br />

by budgeting of these tracers. The flux<br />

gradient method connects changes in the tracer<br />

concentrations in distinct lake layers (budgeting)<br />

to the vertical fluxes. Turbulent diffusion coefficients<br />

are calculated from the fluxes using Fick’s<br />

law.<br />

The results show that the vertical exchange is suppressed<br />

by the stratification. In a small quarry<br />

pond, the heat fluxes are reduced to the conduction<br />

level (∼ 10 −7 m 2 /s) during summer in the<br />

stratified region (high temperature gradients, see<br />

figure). This gives room for even lower transport<br />

rates of solutes.<br />

In a mining lake with a strong permanent salt<br />

stratification we found the molecular diffusion<br />

(∼ 10 −9 m 2 /s) to be the dominant transport process<br />

within the stratified region.<br />

Outlook/Future work A new project will<br />

start in 2006 to investigate the interaction of<br />

groundwater connection, vertical transport and<br />

stratification in a mining lake with a permanent<br />

density gradient maintained by hydrochemical<br />

processes.<br />

Main publication von Rohden [2002]


4.2. LAKE RESEARCH (LIMNOPHYSICS) 165<br />

4.2.3 Investigation of Water Currents in Lake Willersinnweiher using Acoustic<br />

Doppler Current Profiler<br />

Participating scientists Karl Wunderle, Christoph von Rohden, Johann Ilmberger<br />

Abstract In a small stratified lake currents were measured with a bottom mounted 1200 kHz Acoustic<br />

Doppler Current Profiler, ADCP. Currents are measured with an accuracy of ∼1 mm/s and a<br />

vertical resolution of 20-40 cm. Typical current speeds in Lake Willersinnweiher are very low in the<br />

range of several mm/s (especially in the hypolimnion), occasionally reaching a few cm/s during wind<br />

incidents.<br />

Figure 4.10: Short Time Fourier Transformation (STFT) of the east - west component of water<br />

currents at a depth of 10 m. The time series, used for these calculations, startet at the 6th July 2004.<br />

The window for the individual spectrum is 21 h (256 5-minute values) at an overlap of 80%. The color<br />

indicates the spectral intensity of the signal on a logarithmic scale from high (red) to low (blue).<br />

Background Transport and mixing in the interior<br />

of lakes is due to wind driven internal motion.<br />

To investigate the internal dynamics, fluctuations<br />

of water temperature as indirect indicator of motion<br />

and direct water current measurements can<br />

be used.<br />

Funding The work was supported by the SFB<br />

359 “Reaktive Strömungen, Diffusion und Transport”,<br />

University of Heidelberg.<br />

Methods and results Current measurements<br />

were performed with the ADCP (RD Instruments)<br />

mounted at the bottom of the lake. 800 pings were<br />

averaged and recorded every 5 minutes. To keep<br />

the inclination angles below 2 ◦ , it was mounted<br />

in a cardanic suspension. The ADCP was powered<br />

through a cable from ashore, using low cost<br />

rechargeable 60 V battery pack. The cable was<br />

also used to check the operation and <strong>download</strong> the<br />

stored data once a week. In addition to the current<br />

measurements weekly vertical profiles of temperature<br />

and electrical conductivity were taken<br />

and temperature data were continuosly recorded<br />

at several depths at different sites in the lake.<br />

Long term Fourier transform does not show significant<br />

peaks in the spectra i.e. there are no distinct<br />

eigenfrequencies on a longer timescale. In order to<br />

resolve the dynamics of the watercurrents Short<br />

Time Fourier Transform (STFT) was used. Figure<br />

1 shows an example of a STFT calculation<br />

of the east-west component of the watercurrent<br />

from 6th to 13th July 2004 using a window of 21h<br />

(256 5min values) and an overlap of 80The STFT<br />

computations reveal the transient character of the<br />

currents with peaks at ∼3h.<br />

Main publication Wunderle [2005]


166 CHAPTER 4. AQUATIC SYSTEMS<br />

References<br />

Ilmberger, J., & von Rohden, C. 2005. Abschlußbericht zum Forschungsvorhaben: ”SF6 als Tracer<br />

<strong>für</strong> Transport- und Mischungsprozesse in Tagebaurestseen.<br />

Ilmberger, J., von Rohden, C., & Wunderle, K. 2005. Observation of Multilayer Structures in a Small<br />

Lake. In: In A. Folkard and I. Jones,editors, 9th workshop on physical processes in natural waters.<br />

von Rohden, C. 2002. Tracerstudie zur Quantifizierung des Vertikaltransports in meromiktischen Seen.<br />

PhD thesis, University of Heidelberg.<br />

von Rohden, C., & Ilmberger, J. 2001. Tracer experiment with sulfur hexafluoride to quantify the<br />

vertical transport in a meromictic pit lake. aquatic sciences, 63, 417–431.<br />

von Rohden, C., Hauser, A., Wunderle, K., Ilmberger, J., Wittum, G., & Roth, K. 2005. Lake<br />

dynamics: observation and high-resolution numerical simulation. In Rannacher editor. Springer.<br />

Wunderle, K. 2005. Untersuchungen der Strömungen im Willersinnweiher mit einem akustischen<br />

Strömungsmessgerät. Diplomarbeit, University of Heidelberg.


Small-Scale Air-Sea Interaction<br />

5.1 Small-Scale Air-Sea Interaction . . . . . . . . . . . . . . . . . . . . . . . . 169<br />

167


5.1. SMALL-SCALE AIR-SEA INTERACTION 169<br />

5.1 Small-Scale Air-Sea Interaction<br />

Names of group members<br />

Prof. Dr. B. Jähne, head of group<br />

Dr. G. Balschbach, staff<br />

Dipl.Phys. K. Degreif, PhD student<br />

Dipl.Chem. A. Falkenroth, PhD student<br />

Dr. C. S. Garbe, Postdoc<br />

Dipl.Phys. M. Jehle, PhD student<br />

Dipl.Phys. M. Klar, PhD student<br />

Dipl.Phys. C. Popp, PhD student<br />

R. Rocholz, diploma student<br />

Dipl.Phys. M. Schmidt, PhD student<br />

Dr. U. Schimpf, Postdoc<br />

T. Schwarz, diploma student<br />

Abstract Research in small-scale air-sea interaction at the IUP concentrates on air-sea gas exchange<br />

and the dynamics of wind waves. The basic mechanisms are studied in laboratory experiments in a<br />

unique annular wind-wave facility (The Heidelberg Aeolotron) and field experiments using imaging<br />

techniques for quantitative visualization of the water surface structure (wind waves), the flow field,<br />

concentration fields by laser-induced fluorescence, and the water surface temperature by passive and<br />

active thermography.<br />

Scientific Objectives The basic scientific objective is a better physical understanding of air-sea<br />

gas transfer, the dynamics of short wind waves, and the micro turbulence at the ocean surface.<br />

Currently the following topics are investigated:<br />

1. The influence of the diffusion coefficient (or the Schmidt number Sc) on the transfer velocity<br />

of gases. Together with the transfer velocity itself, this is a sensitive measure to distinguish<br />

different models.<br />

2. The influence of wind waves on air-sea gas transfer by enhancing the turbulence near the water<br />

surface.<br />

3. The influence of chemical reactivity on gas transfer. Here the hydration reaction of CO2 is<br />

currently of most interest, because today only some model computations but no detailed measurements<br />

are available.<br />

4. Analysis of the spatial and temporal structure of the turbulence in the water-sided viscous<br />

boundary layer as the driving force for air-water gas exchange.<br />

Overarching topic is the study of small-scale air-sea interaction, especially the mechanisms of<br />

air-sea gas exchange and the dynamics of wind waves.<br />

Background Despite intensive research, knowledge about air-sea interaction processes has not been<br />

significantly improved during the last decade. Many basic questions are still open. The relation of<br />

the air-sea gas exchange rate with wind speed is discussed controversial. Both field and laboratory<br />

experiments show large deviations up to a factor of two from a simple relation between the wind<br />

speed and the gas transfer velocity [Jähne & Haußecker, 1998; Jähne, 2001]. It is obvious that<br />

other parameters, especially wave-induced near-surface turbulence and surface active films are of<br />

importance, but detailed modeling of these processes is still lacking. Therefore, despite their known<br />

significant limitations, semi-empirical relations between the wind speed and the gas transfer velocity,<br />

as established by Liss & Merlivat [1986] or Wanninkhof [1992], are still the state of the art.<br />

Another uncertainty in the estimation of transfer velocity is the dependence on the Schmidt number<br />

Sc. It is common to assume that the transfer velocity k is proportional to Sc −1/2 . However, for quite<br />

some time it has been known [Jähne, 1980] that the exponent is about 2/3 for a smooth water surface<br />

at low wind speeds and gradually decreases to 1/2 for a rough and wavy water surface. The exact<br />

shape of this transition, and especially how it is influenced by surface films in coastal zones and on<br />

which parameters it depends, is not known. This lack of knowledge causes a considerable uncertainty<br />

in estimating the transfer velocity. A change of the exponent from 2/3 to 1/2 without a change of<br />

other parameters causes an increase of the transfer velocity by about a factor of two.


170 CHAPTER 5. SMALL-SCALE AIR-SEA INTERACTION<br />

Recently, the intermittent nature of the gas exchange process has come into the focus of research.<br />

Of particular interest is the microscale wave breaking, a process that causes enhanced near-surface<br />

turbulence. It is known that microscale wave breaking enhances gas transfer. Zappa et al. [2001]<br />

found, e. g., a good correlation between the measured transfer velocity and the fraction of the water<br />

surface at which surface renewal occurred by microscale wave breaking. Details of the mechanisms<br />

that allow a physically-based parameterization are, however, not yet known. The intermittency of the<br />

gas transfer is of much importance when integrating gas transfer rates form short time and spatial<br />

scales as determined by active thermography to larger scales. Because the relation between wind<br />

speed and the transfer velocity and possible other parameters is certainly nonlinear, not only the<br />

mean values but also the variations must be known for a proper integration.<br />

A particularly difficult and interdisciplinary problem is the influence of organic films on air-sea gas<br />

transfer [Frew, 1997]. Surfactants attenuate short wind waves and thus changes the hydrodynamic<br />

boundary conditions at the water surface. In effect, the gas transfer rate is significantly reduced.<br />

Interestingly this complex process can be modeled by simply relating the gas transfer rate to the<br />

mean square wave slope [Frew, 1997; Bock et al. , 1999; Frew et al. , 2004]. This close correlation<br />

between the mean square slope and the gas transfer rate was already pointed out by Jähne et al.<br />

[1987] long before systematic studies of the influence of surface films on gas transfer were performed.<br />

However, a more detailed modeling is still lacking.<br />

Main methods By using novel visualization techniques and image sequence processing techniques,<br />

the complex small-scale air-sea interaction processes can be tackled experimentally for the first time<br />

in both laboratory and field experiments. Equally important are spectroscopic techniques that allow<br />

simultaneous gas exchange measurements with many tracer. The techniques are briefly described in<br />

the following.<br />

UV-spectroscopy for volatile species dissolved in water UV-spectroscopy in contrast to IRspectroscopy<br />

offers the significant advantage that it is not required to degas water samples in<br />

order to measure gases and volatile species dissolved in water, because water is transparent in<br />

the required wavelength range from 200–300 nm. Thus this technique can be used to measure<br />

concentrations both the water and air space. The technique adds a number of volatile species for<br />

gas exchange measurements, especially species containing aromatic rings, such as fluorobenzenes,<br />

thiophenes, and pyrenes. For further details see section 5.1.3.<br />

Wave slope and height imaging A detailed investigation of the dynamics of short wind waves<br />

required simultaneous imaging of the wave height and slope. This is because the energy of<br />

gravity waves is contained in the wave height whereas the energy of the capillary waves is<br />

proportional to the wave slope. Therefore a novel instrumentation was developed that is capable<br />

to measure the wave slope and height simultaneously by making use of the fact that light at<br />

different wavelengths in the near infrared shows significant differences in absorption. In this way<br />

the imaging wave slope gauge could be extended for simultaneous wave height measurements<br />

(section 5.1.7 and Jähne et al. [2005c]).<br />

Active thermography Using heat as a proxy tracer for gases has two significant advantages. Firstly,<br />

the concentration of the tracer at the water surface can directly be measured with infrared cameras.<br />

Secondly, the heat flux can be controlled by applying infrared radiation onto the water<br />

surface. Periodically varying infrared radiation was applied to the water surface to create a corresponding<br />

variation in the surface temperature of the water. For slow variations of the infrared<br />

radiation - slower than the time constant for the exchange process - the transfer velocity can be<br />

measured directly by dividing the known flux density by the measured temperature variation.<br />

If the heat flux is switched off, the temperature increase will decay with the characteristic time<br />

constant t⋆ (surface renewal time) for the transport process across the aqueous heat boundary<br />

layer. From this time constant the transfer velocity k can be computed directly using the relation<br />

t⋆ = D/k 2 , where D is the diffusion coefficient for heat [Jähne et al. , 1989]. By measuring<br />

the phase shift and amplitude damping of the thermal boundary to periodically changing IR<br />

radiation, it is also possible to distinguish between different models for the exchange process<br />

and to investigate the intermittency of the process. Because the infrared image sequences contain<br />

significant contrast, the surface flow field including its vorticity and local convergence and<br />

divergence zones can also be computed from image sequences [Garbe et al. , 2003]. Moreover,<br />

the spatial structure of the micro-turbulence at the water surface can be studied [Schimpf et al.<br />

, 2004].


5.1. SMALL-SCALE AIR-SEA INTERACTION 171<br />

Fluorescence imaging of gas tracer concentration fields The fluorescence spectrum of dissolved<br />

dyes generally shows a bandwidth between 30 and 100 nm. A second dye is used to attenuate<br />

the emitted fluorescent light in this wavelength range differently for different wavelengths. With<br />

this double-dye technique, the shape of the observed fluorescence spectrum depends on the path<br />

length the light travels through the water before it is measured. Because the fluorescence is<br />

excited from the air space, the path length directly corresponds to the distance from the water<br />

surface.<br />

For a given wavelength, the fluorescent light received is then integrated over a characteristic<br />

depth ˆz = α −1 (λ), where α(λ) is the wavelength-dependent absorption coefficient of the absorbing<br />

dye solution. If α(λ) is known, the depth-dependent concentration can be computed from<br />

the measured spectra as a linear inverse problem.<br />

This technique is investigated for the quenching of the fluorescence of a organic rutheniumcomplex<br />

by oxygen (section 5.1.6) and pH-dependent fluorescent dyes (section 5.1.8).<br />

3-D flow measurements close to and at the water surface The aqueous viscous boundary layer<br />

at a wind-driven water surface has a thickness of at most a millimeter. Therefore almost no flow<br />

measurements are available from this layer at a free water surface. We try to tackle this difficult<br />

experimental problem with two techniques. First, thermal image sequences from the water surface<br />

contain enough structures to computed 2-D flow fields (section 5.1.2). Secondly, a modified<br />

particle tracking technique is used for depth-resolved flow measurements. Again an absorbing<br />

dye is used to code the depth of the tracked particles and to measure the velocity component<br />

perpendicular to the water surface from the brightness change of the particle (section 5.1.5).<br />

Main activities Our current main activities include<br />

1. the development of a novel optic technique for simultaneous imaging of the height and slope of<br />

short wind waves (section 5.1.7),<br />

2. the development of depth-resolving imaging technique to measure concentration fields of gases<br />

close to the water surface by using a double dye laser induced fluorescence techniques (sections<br />

5.1.6 and 5.1.8),<br />

3. detailed studies of the Schmidt number dependency of air-water gas transfer (section 5.1.3),<br />

4. investigations of the air-sea gas exchange by active thermography (section 5.1.1),<br />

5. analysis of flow fields by passive and active thermography thermography (section 5.1.2),<br />

6. 3-D flow measurements within the aqueous viscous boundary layer (section 5.1.5), and<br />

7. 3-D flow measurements within porous gravel layers (section 5.1.4).<br />

Funding<br />

1. DFG-Schwerpunktprogramm 1114 “Mathematische Methoden der Zeitreihenanalyse und digitalen<br />

Bildverarbeitung”<br />

2. DFG-Schwerpunktprogramm 1147 “Bildgebende Strömungsmesstechnik”<br />

3. Graduiertenkolleg 1114 “Optische Messtechniken <strong>für</strong> die Charakterisierung von Transportprozessen<br />

an Grenzflächen” (TU Darmstadt and U Heidelberg)<br />

4. DFG Ja395/10: ”Mechanismen des Gasaustausches zwischen Atmosphäre und Ozean: Laborversuche<br />

und Modellierung”<br />

5. DFG Ja395/13: ”Impact of Wind, Rain, and Surface Slicks on Air-Sea CO2 Transfer Velocity -<br />

Tank Experiments”<br />

6. Bundesanstalt <strong>für</strong> Wasserbau


172 CHAPTER 5. SMALL-SCALE AIR-SEA INTERACTION<br />

Cooperation<br />

1. Prof. T. Aach, <strong>Institut</strong> <strong>für</strong> Signalverarbeitung und Prozessrechentechnik, <strong>Universität</strong> Lübeck<br />

2. Prof. Dr. Klaus Affeld, Dr. Ulrich Kertzscher, Labor <strong>für</strong> Biofluidmechanik, <strong>Universität</strong>sklinikum<br />

Charite Berlin, Humboldt <strong>Universität</strong> Berlin<br />

3. Dr. Erhardt Barth, <strong>Institut</strong> <strong>für</strong> Neuro- und Bioinformatik, <strong>Universität</strong> Lübeck<br />

4. Dr. Volker Beushausen, Laser-Laboratorium Göttingen e.V.<br />

5. Dr. Nelson M. Frew, Marine Chemistry and Geochemistry, Woods Hole Oceanographic <strong>Institut</strong>ion<br />

(WHOI), USA<br />

6. Prof. Dr. Tetsu Hara, Graduate School of Oceanography (GSO), University of Rhode Island,<br />

USA<br />

7. Dr. V. Kudryavtsev, Marine Hydrophysical <strong>Institut</strong>e, Sebastopol, Ukraine<br />

8. Dr. V. K. Makin, Royal Netherlands Meteorological <strong>Institut</strong>e, de Bilt, Niederlande<br />

9. Prof. R. Mester, Digitale Bildverarbeitung, <strong>Institut</strong> <strong>für</strong> Angewandte Physik, <strong>Universität</strong> Frankfurt<br />

10. Dr. Bernd Schneider, Dr. Joachim Kuss, <strong>Institut</strong> <strong>für</strong> Ostseeforschung, Warnemünde<br />

11. Prof. Dr. Detlef Stammer, Dr. Martin Gade, <strong>Institut</strong> <strong>für</strong> Meeresforschung, <strong>Universität</strong> Hamburg<br />

12. Prof. Christoph Schnörr, Bildverarbeitung, Mustererkennung & Computergrafik <strong>Universität</strong><br />

Mannheim<br />

13. Prof. Jürgen Wolfrum, PD Dr. Volker Ebert, Physikalische Chemie, <strong>Universität</strong> Heidelberg<br />

Future Work Future work in the coming year will include extension laboratory measurements in the<br />

Heidelberg Aeolotron and the Hamburg wind-wave facility that combine gas exchange, wave imaging<br />

and flow measurements.<br />

The second focus will be further development of the depth-resolving measurements of concentration<br />

fields and 3-D flow fields within the aqueous viscous boundary layer.<br />

Publications<br />

Peer Reviewed Publications<br />

1. Frew et al. [2004]<br />

2. Garbe et al. [2004a]<br />

3. Jähne et al. [2005c]<br />

4. Schimpf et al. [2004]<br />

5. Zhang & Garbe [2004]<br />

Other Publications<br />

1. Jähne [2004]<br />

2. Jähne [2005a]<br />

3. Jähne [2005b]<br />

Doctoral Theses<br />

1. Fuß [2004]<br />

2. Hilsenstein [2004]<br />

3. Klar [2005]<br />

4. Nielsen [2004]


5.1. SMALL-SCALE AIR-SEA INTERACTION 173<br />

Diploma Theses<br />

1. Rocholz [2005]<br />

2. Schwarz [2005]<br />

Invited Talks<br />

1. Jähne [2004]<br />

2. Jähne [2004]<br />

3. Jähne & Garbe [2004]<br />

4. Jähne et al. [2005]


174 CHAPTER 5. SMALL-SCALE AIR-SEA INTERACTION<br />

5.1.1 Investigation of transport processes across the sea-surface microlayer<br />

by active thermography<br />

Participating scientist Uwe Schimpf and Christopher Popp<br />

Abstract The thermal boundary layer is considered as a black box in linear system theory. The<br />

input is a periodically varying heat flux forced onto the water surface by a carbon dioxide laser, the<br />

output is the amplitude and phase shift of the water surface temperature measured by an infrared<br />

camera.<br />

100 Watts CO 2 laser (10.6 µm)<br />

IR camera<br />

(3-5 µm)<br />

240 cm<br />

100 cm<br />

Paddle<br />

temperature probe<br />

humidity probe<br />

temperature probe<br />

62 cm<br />

X-Y scan unit<br />

flow meter<br />

wind direction<br />

wind speed 1.4 m/s<br />

wind speed 3.2 m/s<br />

wind speed 8.2 m/s<br />

Figure 5.1: Setup of the controlled flux technique in the AEOLOTRON wind-wave facility. A carbon<br />

dioxide laser forces a periodic heat flux onto the water surface. The temperature response of the water<br />

surface is measured by an infrared imager. From the image sequences the amplitude damping and the<br />

phase shift of the temperature signal is calculated.<br />

Background In order to improve the parameterizations<br />

and the models of air-gas exchange,<br />

the transport mechanisms in the boundary layer<br />

and their space and time scales have to be understood<br />

in detail. The active controlled flux technique<br />

[Jähne et al. , 1989] gives a detailed insight<br />

into the turbulent processes controlling the transport<br />

across the sea surface microlayer.<br />

Funding Aktives Thermografie System, HBFG-<br />

125-667 (Hardware), DFG Ja395/13-1 (Joint<br />

project with Detlef Stammer, Insitut <strong>für</strong><br />

Meereskunde, <strong>Universität</strong> Hamburg)<br />

Methods and results Heat is used as a proxy<br />

tracer for gases. The heat flux is controlled by<br />

forcing infrared radiation onto the water surface<br />

and the temperature variation is directly measured<br />

with an infrared imager. For slow temporal<br />

variations of the infrared radiation the transfer velocity<br />

is given by the ratio of the heat flux density<br />

and the temperature variation at the water surface.<br />

If the heat flux is switched off, the temperature<br />

increase will decay with a characteristic time<br />

constant of the transport across the thermal sublayer.<br />

The measured phase shifts clearly indicate<br />

that the transfer process is strongly intermittent.<br />

Outlook/Future work The developed system<br />

will be deploy in the DFG project ”Impact of<br />

Wind, Rain, and Surface Slicks on Air-Sea CO2<br />

Transfer Velocity - Tank Experiments” in cooperation<br />

with the <strong>Institut</strong>e of Oceanography, University<br />

of Hamburg. The goal is to improve the<br />

understanding of the parameterization of air-sea<br />

gas exchange with emphasis on CO2.<br />

Main publication Schimpf et al. [2004]


5.1. SMALL-SCALE AIR-SEA INTERACTION 175<br />

5.1.2 Water flow measurements in environmental and biological systems<br />

Participating scientist Christoph S. Garbe<br />

Abstract Novel measurement techniques are developed for accurately determining water flows in<br />

biological and environmental systems. These techniques are closely linked to the development of refined<br />

image processing techniques, making temporally and spatially highly resolved field measurements<br />

feasible.<br />

a) b) c)<br />

Figure 5.2: In a) a thermal image of the air-water interface is shown with the extracted motion field.<br />

In b) the motion of a microfluidic application is shown, and in c) the flow velocity of Xylem in a plant<br />

leaf can be seen.<br />

Background For a number of exchange processes<br />

both in environmental and life sciences, the<br />

transport of water plays a fundamental role. Systems<br />

of interest are turbulent transport at water<br />

surfaces for air sea heat and gas exchange, water<br />

flow in plant leaves, and microfluids. Density<br />

distributions of tracers are visualized with modern<br />

cameras and their motion as well as density<br />

changes estimated from digital image processing<br />

techniques. Examples of such tracers are heat<br />

which can be applied with lasers and visualized<br />

with highly resolved thermographic imagers or<br />

caged dyes for microfluidic applications. Results<br />

of these flow measurements can be used for modelling<br />

physical transport processes, deepening our<br />

understanding of the systems analyzed.<br />

Funding Research Centre Jülich (Forschungszentrum<br />

Jülich), Jülich<br />

DFG SPP 1147, “Bildgebende Messverfahren <strong>für</strong><br />

die Strömungsanalyse”<br />

DFG SPP 1114, “Mathematische Methoden<br />

der Zeitreihenanalyse und digitalen Bildverarbeitung”<br />

Methods and results A fluid is visualized using<br />

density distributions as tracers. These can be<br />

heat or dyes. At the air-water interface, usually<br />

a net heat flux is present which allows visualizing<br />

turbulences directly without additional tracers.<br />

The motion of density distributions is then<br />

modelled as a linear partial differential equation<br />

(PDE). These PDEs can be solved from the image<br />

sequences with techniques developed in digital<br />

image processing. This allows to estimate the<br />

motion as well as density changes in the image<br />

sequences. Through estimating motion as well as<br />

other parameters of the transport model, a deeper<br />

understanding of the transport processes involved<br />

can be reached. Through this technique, the net<br />

heat flux at the air-water interface was estimated<br />

directly for the first time, both temporally and<br />

spatially highly resolved. Furthermore, the flow<br />

of water in plant leaves was also measured in a<br />

relatively simple set-up.<br />

Outlook/Future work The developed techniques<br />

will be used for studying transport processes<br />

for shear driven as well as convective driven<br />

exchange of heat and mass at the air-water interface.<br />

Furthermore, the transport of Xylem in<br />

plant leaves will be measured under varying environmental<br />

forcings. This will make spatially resolved<br />

measurements of water flows in plant leaves<br />

possible for the first time, closing a missing link<br />

in the understanding of water relations in plants.<br />

The low Reynolds number flows in microfluidic<br />

mixing machines will also be measured, allowing<br />

to improve the design and mixing capabilities for<br />

such devices.<br />

Main publication Garbe et al. [2004a]; Zhang<br />

& Garbe [2004]; Garbe et al. [2004b]


176 CHAPTER 5. SMALL-SCALE AIR-SEA INTERACTION<br />

5.1.3 Time resolved Measurements of Air Water Gas Exchange<br />

Participating scientist Kai Degreif<br />

Abstract Laboratory measurements are performed to determine the influence of short wind waves<br />

on air-sea gas exchange. UV-spectroscopy is introduced as a powerful method for tracking the fate<br />

of gaseous and volatile tracers simultaneously both in the gas and water phase. The “controlled<br />

leakage technique”, a new measurement technique that permits the calculation of time resolved flux<br />

rates exclusively from the air-side concentration, could be validated within the scope of the UVmeasurements.<br />

Reliable gas flux measurements of dissolved trace gases for a broad range of species<br />

without the need for extraction are now feasible.<br />

a b<br />

d e<br />

wind speed [m/s]<br />

relative concentration<br />

5<br />

4<br />

3<br />

2<br />

1<br />

0<br />

0 1 2 3<br />

time[h]<br />

4 5 6<br />

0.9<br />

0.8<br />

0.7<br />

0.6<br />

0.5<br />

0.4<br />

0.3<br />

0.2<br />

0.1<br />

measured concentration<br />

calculated concentration<br />

0<br />

0 1 2 3<br />

time [h]<br />

4 5 6<br />

c<br />

f<br />

relative concentration<br />

transfer velocity k [cm/h]<br />

0.14<br />

0.12<br />

0.1<br />

0.08<br />

0.06<br />

0.04<br />

0.02<br />

0 1 2 3<br />

time [h]<br />

4 5 6<br />

25<br />

20<br />

15<br />

10<br />

5<br />

0<br />

0 1 2 3<br />

time [h]<br />

4 5 6<br />

Figure 5.3: Time resolved gas exchange measurements at the small Heidelberg Wind Wave Facility. a<br />

Experiments are performed in a small circular water channel of 1.2 m diameter. b Rotating windpaddles<br />

produce controlled wind speeds. c The investigated trace gases are dissolved in the water phase.<br />

The air-volume being constantly flushed with fresh air, the air-side concentration of the released tracers<br />

is proportional to the gas transfer and the water concentration. d Concentration measurements of<br />

volatile aromatics are performed using UV-spectroscopy simultaneously in the air and water phase. e<br />

The calculated water concentration is in good agreement with the measured water concentration. f<br />

Gas transfer velocities are achieved with a high time resolution.<br />

Background The oceans can act as a source<br />

or sink for climate relevant gases such as carbon<br />

dioxide, methane or dimethylsulphide. As hydrodynamics<br />

at the free oceans surface is not well<br />

understood yet, the estimation of total flux rates<br />

of those gases has to rely on empiric parameterizations.<br />

Precise and systematic laboratory measurements<br />

can help us to get a better understanding<br />

of the gas transfer rates dependence on tracer<br />

parameters like Schmidt number and solubility or<br />

hydrodynamic parameters like wind stress, waviness<br />

of the water surface and turbulence intensity.<br />

Methods and results Conventional gas exchange<br />

measurements rely on the knowledge of<br />

concentration gradients across the water surface.<br />

Therefore the information about the concentration<br />

of the dissolved species is indispensable. UVspectroscopy<br />

provides the possibility for direct<br />

and fast measurement of multiple tracer concentrations<br />

both in the water and the atmosphere.<br />

Volatile aromatic hydrocarbons such as benzene,<br />

thiophene, pyridine and derivates, and some other<br />

species can be measured.<br />

The “controlled leakage technique” permits the reconstruction<br />

of the water concentration from gases<br />

that are released by the water body only by measuring<br />

the air concentration. Therefore flux rates<br />

of tracers with a wide range of physicochemical<br />

parameters, i.e. Schmidt number and solubility<br />

can be measured simultaneously so that a detailed<br />

experimental study of the influence of these parameters<br />

on air-water gas exchange has now become<br />

feasible and will be presented within the<br />

work.<br />

Funding Project funded by the DFG<br />

Main publication Degreif, Kai, Doktorarbeit,<br />

<strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong> und Interdisziplinäres<br />

Zentrum <strong>für</strong> Wissenschaftliches Rechnen, <strong>Universität</strong><br />

Heidelberg, 01/2006


5.1. SMALL-SCALE AIR-SEA INTERACTION 177<br />

5.1.4 3-D flow measurements within a porous gravel layer<br />

Participating scientist Michael Klar<br />

Abstract A novel technique for 3-D flow measurements within a permeable gravel layer is developed.<br />

Two fiberoptic endoscopes are used in a stereoscopic arrangement to acquire image sequences of<br />

the flow field within a single gravel pore. The images are processed by a 3-D Particle-Tracking<br />

Velocimetry (3-D PTV) algorithm, which yields the three-dimensional reconstruction of Lagrangian<br />

particle trajectories.<br />

Figure 5.4: Left: Experimental setup with two fiberoptic endoscopes observing the flow field within a<br />

specially prepared artificial gravel pore. Right: 3-D flow trajectories of the pore flow, obtained from<br />

the recorded stereo image sequences.<br />

Background Bed stability of rivers and waterways<br />

is one of the major issues of geotechnical and<br />

hydraulic engineering. The design of erosion protection<br />

structures, e.g. filter layers of noncohesive<br />

gravel, is based on empirical design criteria and<br />

numerical, analytical and phenomenological models<br />

for flow and sediment transport. There is a<br />

lack of experimental data that can be used to validate<br />

and improve these models. A detailed examination<br />

of the hydrodynamic processes that cause<br />

instability of single grains requires flow measurements<br />

with a high temporal and spatial resolution.<br />

Funding Federal Waterways Engineering and<br />

Research <strong>Institut</strong>e (Bundesanstalt <strong>für</strong> Wasserbau,<br />

BAW), <strong>Karls</strong>ruhe.<br />

Methods and results The core of the experimental<br />

setup is an artificial gravel pore made up<br />

of grains fixed to each other. Optical access to the<br />

pore volume is given by two flexible fiberoptic endoscopes.<br />

The artificial pore is embedded within a<br />

gravel bed at the bottom wall of an open-channel<br />

flow. Tracer particles are added to visualize the<br />

pore flow, and image sequences of the flow field<br />

inside the artificial pore are recorded.<br />

Analysis of the image sequences by digital image<br />

processing techniques, namely a 3-D PTV algorithm,<br />

yields the Lagrangian flow velocities of the<br />

tracer particles along their trajectories. The algorithm<br />

is based on stereo correlation of the particle<br />

trajectories. The 3-D coordinates are calculated<br />

by triangulation of corresponding optical<br />

rays. Correlating 2-D trajectories instead of the<br />

positions of single particles allows for a simple<br />

setup with a minimum number of two cameras<br />

resp. endoscopes.<br />

Experiments have been conducted in cooperation<br />

with the Federal Waterways Engineering and Research<br />

<strong>Institut</strong>e (Bundesanstalt <strong>für</strong> Wasserbau,<br />

BAW) in Karlruhe and the <strong>Institut</strong>e for Hydromechanics<br />

of the University of <strong>Karls</strong>ruhe. Extensive<br />

flow measurements under different flow conditions<br />

have been carried out in an experimental flume located<br />

at the BAW. The impact of the turbulent<br />

free surface flow on the pore flow inside the gravel<br />

bed is clearly reflected in the measurement results.<br />

These studies are part of an international research<br />

project initiated by the BAW, with the objective<br />

to quantify the influence of turbulent velocity and<br />

pressure fluctuations on the stability of river beds.<br />

Outlook/Future work The main subject of<br />

further work will be the comprehensive hydromechanic<br />

analysis of the flow data obtained in the<br />

experiments at the BAW.<br />

Main publication Klar [2005]


178 CHAPTER 5. SMALL-SCALE AIR-SEA INTERACTION<br />

5.1.5 3D fluid flow measurement close to surfaces<br />

Participating scientist Markus Jehle<br />

Abstract A novel measurement technique for 3D reconstruction of Eulerian velocity vector fields<br />

and Lagrangian trajectories at water-side boundary layers in wavy free surfaces is developed. In a<br />

first step, the method is applied in a falling film with known velocity profile.<br />

intensity [arbitrary units]<br />

1<br />

0.9<br />

0.8<br />

0.7<br />

0.6<br />

0.5<br />

0.4<br />

0.3<br />

0.2<br />

0.1<br />

0<br />

absorption of dye (tartracine)<br />

emission of LED 1 ("royal blue")<br />

emission of LED 2 ("blue")<br />

380 400 420 440 460 480 500 520 540<br />

wavelength [nm]<br />

Figure 5.5: Top: Experimental setup. Bottom:<br />

The emitted light of the two types of LEDs<br />

(“blue” and “royal blue”) is absorbed by the dye<br />

(tartracine acid yellow) unequally. Thus, with<br />

known penetration depths, a reconstruction of the<br />

depth of the observed particle is possible.<br />

Background In order to examine the air-water<br />

gas exchange, a detailed knowledge of the waterside<br />

flow-field is needed. Therefore important<br />

quantities like wall-shear stresses, velocity profiles,<br />

dissipation rates and Lagrangian trajectories,<br />

have to be determined. Because the flow<br />

is 3D, instationary and close to the wave-driven<br />

(curved and moving) water-surface, conventional<br />

techniques like Particle Imaging Velocimetry using<br />

laser light sections are not applicable. A technique<br />

that is similar to the one proposed here is<br />

applied in the field of biofluidmechanics succesfully,<br />

where it is important to get knowledge about<br />

the flow in (artificial) blood vessels.<br />

Methods and results A fluid volume is illuminated<br />

by LEDs. Small glas hollow spheres (mean<br />

diameter 30µm) are added to the fluid, working as<br />

tracer. A high speed camera pointing to the water<br />

surface from above records the image sequences.<br />

The depth of an individual fluid particle is coded<br />

by a supplemented dye, which absorbs the light of<br />

the LEDs obeying Beer-Lambert’s law. By using<br />

LEDs flashing with two different wavelengths it is<br />

possible to use particles variable in size:<br />

The depth of a particle, which appears to the camera<br />

under the intensities (gray values) g1 and g2<br />

is calculated according to<br />

z(g1, g2) = z∗1z∗2<br />

z∗1 − z∗2<br />

�<br />

ln<br />

� g1<br />

g2<br />

�<br />

+ ln<br />

� g02<br />

g01<br />

��<br />

,<br />

where z∗1 and z∗2 are the penetration depths of<br />

LED-light of two distinct wavelengths into the<br />

dyed fluid, and g01/g02 is the ratio of the intensities<br />

of the two light sources. All of these quantities<br />

can be obtained by means of calibration.<br />

The velocity vectors of the flow are obtained using<br />

an extension of the method of optical flow,<br />

allowing for exponential brightness changes.<br />

First results obtained in a laminar falling film<br />

with known hydrodynamics show the feasibility<br />

of this measurement technique: the measurement<br />

reproduces the theoretical velocity profile in good<br />

agreement.<br />

Outlook/Future work The method will be extended<br />

to higher particle densities, coping with<br />

the problem of overlapping of the motion of individual<br />

particles. Further, the technique will be<br />

applied both at curved and at moving free surfaces.<br />

Simultaneous measurements using active<br />

thermography and imaging slope gauge will be<br />

conducted.<br />

Funding DFG-Schwerpunktprogramm 1147


5.1. SMALL-SCALE AIR-SEA INTERACTION 179<br />

5.1.6 Imaging concentration profiles of water boundary layer by Double-<br />

Dye LIF<br />

Participating scientist Achim Falkenroth<br />

Abstract Laser-Induced Fluorescence (LIF) is applied to directly observe and understand the mechanism<br />

of gas exchange in the upper 500 µm boundary layer. The luminescent dye used (Ru-complex)<br />

is sensitive to a given in-situ oxygen concentration that quenches the phosphorescence. The new<br />

Double-Dye LIF technique strives for a 2-D spatial resolution of 200x50 µm 2 .<br />

Figure 5.6: The camera looks through a prism on the surface to measure a wavelength spectrum for<br />

every point of a laser line. Spectra with and without the second dye are shown on the left.<br />

Background The difficulty in studying the<br />

inter-phase exchange processes is due to the small<br />

interacting thickness of approximately 30 µm to<br />

1 mm on both sides of a boundary layer z∗. Therefore,<br />

none of the traditional fixed sampling methods<br />

are applicable.<br />

A non invasive optical method using luminescent<br />

dyes is chosen to determine the gas concentration.<br />

Especially phosphorescent dyes are advantageously<br />

sensitive to quenching because of the long<br />

live time of their excitation states. In regions of<br />

high oxygen concentration, the amount of light<br />

emitted will be significantly lower.<br />

Fluorescent pH indicators may also be used, as<br />

they are able to quantitatively visualise acid or<br />

basic gases like HCl, NH3, or CO2. In former<br />

studies, the boundary layer of the water was monitored<br />

sideways. This way, it is difficult to get a<br />

high resolution with a wavy and agitated surface.<br />

Methods and results The idea of this work is<br />

to reconstruct the concentration profile by looking<br />

from the top on the surface using the spectral<br />

information of all points illuminated by a visible<br />

laser system. The light emitted by the luminescent<br />

dye travels back to the surface through the<br />

water body.<br />

A second dye is dissolved which absorbs certain<br />

wavelengths of the emission spectrum. Therefore,<br />

the deepness information is concealed in the light<br />

spectra. By applying an inverse modelling approach,<br />

the concentration depths can be evaluated<br />

over the whole depth profile.<br />

The time resolution aimed for is naturally predetermined<br />

by the demanding task to catch the<br />

micrometer waves and turbulence events like, for<br />

example, surface renewal. Finally, a temporal resolution<br />

of 30 − 100 Hz should be reached.<br />

First results are luminescence spectra of about 300<br />

pixels acquired with a low noise camera. The signal<br />

appears to be adequate as an input for the<br />

inverse calculation in order to gain the concentration<br />

profiles.<br />

Outlook/Future work The consistent next<br />

steps will be to improve the resolution and stability<br />

of the reconstruction. The application of this<br />

method for measurements in a water tank with<br />

wind generated waves lies ahead.<br />

Funding DFG-Research-Training-Group<br />

(Graduiertenkolleg 1114)


180 CHAPTER 5. SMALL-SCALE AIR-SEA INTERACTION<br />

5.1.7 Combined slope/height measurements of short wind waves : ISHG<br />

Participating scientists Roland Rocholz, Martin Schmidt<br />

Abstract A new technique for the simultaneous measurement of wave height and wave slope of<br />

water surface waves has been developed. The Imaging Slope/Height Gauge (ISHG) is an imaging<br />

system that is designed to measure waves at different length scales. Using a high speed camera, the<br />

high spatiotemporal resolution provides an insight into hydrodynamic processes such as microscale<br />

wave breaking and small scale wave-wave interaction.<br />

f 2<br />

high speed camera<br />

(lens set to infinity)<br />

lens (L 2 ) for telecentric<br />

imaging (f 2 = 50 cm)<br />

water body<br />

lens (L 1 ) for telecentric<br />

illumination (f 1 = 25 cm)<br />

diffusing screen<br />

rays are only<br />

for illustration<br />

(entrance pupil of the<br />

camera lies at the focal<br />

point of lens L 2 )<br />

f 2 (mean water height is at<br />

focal distance to L 2 )<br />

water height<br />

(6 to 16 cm)<br />

f 1 (diffusing screen is at<br />

focal distance to L 1 )<br />

programmable LED-array<br />

(320x1W, λ = 880nm)<br />

Figure 5.7: Sketch of the wave imaging system<br />

for the simultaneous measurement of waves height<br />

and slope.<br />

Background Since water surface waves<br />

strongly influence transfer velocities due to the<br />

induced turbulence, such wave measurements are<br />

used for monitoring the conditions in gas exchange<br />

experiments. Unfortunately, the slope calibration<br />

of typical imaging wave measurement techniques<br />

like the color imaging slope gauge used at the<br />

Heidelberg Aeolotron so far is depending on the<br />

wave height of larger waves. To overcome this<br />

source of systematic errors, a new technique is<br />

under development with the following aims:<br />

• The slope of the waves should be measured<br />

without biases due to the wave height<br />

• The image size should not change with wave<br />

height<br />

• The wave slope and height should be measured<br />

simultaneously<br />

• Simple set-up with a single camera<br />

Funding DFG, Ja395/13: ”Mechanismen des<br />

Gasaustausches zwischen Atmosphäre und Ozean:<br />

Laborversuche und Modellierung”<br />

Methods and results Like the color imaging<br />

slope gauge the slope measurement of the new<br />

Imaging Slope/Height Gauge (ISHG) is based on<br />

light refraction (shape from refraction) and makes<br />

use of an area-extended light source with defined<br />

spatial variation of radiance, produced by a programmable<br />

LED array. This Imaging Slope Gauge<br />

gives a 2-D slope map of the water surface. The<br />

Imaging Height Gauge gives the 2-D height map.<br />

This is also used to correct the slope map for<br />

height dependencies. The method is based on<br />

light absorption and works with light in the near<br />

infrared range. The optical setup provides a telecentric<br />

imaging. The camera is virtually located<br />

at infinity so that height variations of the water<br />

surface do not affect the image scaling.<br />

Outlook/Future work The ISHG system at<br />

our small wind wave flume is still under construction.<br />

The calibration and first wave measurements<br />

are expected to take place at the end of year 2005.<br />

It is planned to assemble the same system at the<br />

wind-wave tank of the University of Hamburg and<br />

at the wind-wave facility AEOLOTRON, University<br />

of Heidelberg. Combining the ISHG with infrared<br />

imaging will be the next step of extending<br />

the system.<br />

Main publication Jähne et al. [2005c]


5.1. SMALL-SCALE AIR-SEA INTERACTION 181<br />

5.1.8 Development of a depth resolving boundary layer visualization for<br />

gas exchange at free water surfaces<br />

Participating scientist Tobias Schwarz<br />

Abstract To directly visualize gas concentration transport in the water-sided boundary layer, a<br />

combined LIF-measurement system consisting of a laser scanning unit and a confocal microscope has<br />

been developed and constructed. Furthermore, methods to reconstruct a 2-D depth profile had been<br />

investigated.<br />

Figure 5.8: An example of the fluorescence intensity changes through local gas concentrations, illuminated<br />

with the laser scanning system.<br />

Background As detailed knowledge of gas exchange<br />

between atmosphere and ocean is of great<br />

importance for predicting and modeling future<br />

climate situations, this diploma thesis aimed at<br />

the development of a measurement system for improved<br />

gas exchange measurements.<br />

Funding Graduiertenkolleg 1114 “Optische<br />

Messtechniken <strong>für</strong> die Charakterisierung von<br />

Transportprozessen an Grenzflächen” (TU Darmstadt<br />

and U Heidelberg)<br />

Methods and results A measurement setup<br />

is introduced which makes it possible to directly<br />

measure two-dimensional, vertical concentration<br />

profiles of gases in the water sided boundary layer<br />

using Laser-Induced Fluorescence (LIF). While it<br />

is impossible to gain knowledge of the physical<br />

processes involved in gas exchange using measurements<br />

of transfer rates and mass balances, the introduced<br />

method makes it possible to directly visualize<br />

the physical processes of matter transport<br />

in the layer. The measurement method is based on<br />

two basic principles: First, a fluorescence indicator<br />

is used, whose fluorescence intensity is proportional<br />

to the local pH-value, thus allowing a spa-<br />

tial resolved measurement of the concentrations of<br />

dissolved alkaline or acidic gases. Second, to create<br />

a depth resolution, a second, absorbing dye is<br />

added, whose absorption maximum lies inside the<br />

fluorescence spectrum, so that spectra from different<br />

depths show changes in their spectral shape<br />

due to the different light path lengths through the<br />

absorber. Thus the measured spectrum is the superposition<br />

of all depth spectra, which provide the<br />

basis of a linear inverse problem. Models for the<br />

reconstruction of the depth information will be introduced<br />

in the course of this thesis, and the solvability<br />

will be analyzed. As the stability of the<br />

solution of the inverse problem is almost exclusively<br />

determined by the invertibility of the basis<br />

function matrix, a confocal microscope was constructed,<br />

which allowed the direct measurement of<br />

depth spectra. Thereby it was made possible to<br />

numerically analyze and evaluate the conditioning<br />

of the matrix invertibility.<br />

Outlook/Future work Work to be continued<br />

within Graduiertenkolleg 1114<br />

Main publication Schwarz [2005]


182 CHAPTER 5. SMALL-SCALE AIR-SEA INTERACTION<br />

References<br />

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and short wind waves. J. Gephys. Res., 104, 25 821–25 831.<br />

Frew, N. M. 1997. The role of organic films in air-sea gas exchange. Pages 121–172 of: Liss, Peter S., &<br />

Duce, Robert S. (eds), The Sea Surface and Global Change. Cambridge, UK: Cambridge University<br />

Press.<br />

Frew, N. M., Bock, E. J., Schimpf, U., Hara, T., Haußecker, H., Edson, J. B., McGillis, W. R., Nelson,<br />

R. K., McKeanna, B. M., Uz, B. M., & Jähne, B. 2004. Air-sea gas transfer: its dependence on wind<br />

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Fuß, D. 2004. Kombinierte Höhen- und Neigungsmessung von winderzeugten Wasserwellen am Heidelberger<br />

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Infrared Image Sequences. J. Mathematical Imaging and Vision, 19, 159–174.<br />

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Encyclopedia of Ocean Sciences. Academic Press, London.<br />

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Ocean, A Contribution to the SOLAS Project. Invited talk, Hauptvortrag Fachverband <strong>Umweltphysik</strong>,<br />

DPG Frühjahrstagung München, 22. Mrz 2004.<br />

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Conference on Quantitative Infrared Thermography, von Karman <strong>Institut</strong>e for Fluid Dynamics in<br />

Rhode Saint Genèse, Belgium, 08. July 2004.<br />

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influencing air/water gas exchange. J. Geophys. Res, 92, 1937–1949.<br />

Jähne, B., Libner, P., Fischer, R., Billen, T., & Plate, E. J. 1989. Investigating the transfer processes<br />

across the free aqueous viscous boundary layer by the controlled flux method. Tellus, 41B, 177–195.<br />

Jähne, B., Nielsen, R., Popp, C., Schimpf, U., & Garbe, C. S. 2005. Air-Sea Gas Transfer: Schmidt<br />

Number Dependency and Intermittency. Invited talk, 37th International Liège Colloquium on Ocean<br />

Dynamics Gas Transfer at Water Surfaces, 2–6 May 2005.


5.1. SMALL-SCALE AIR-SEA INTERACTION 183<br />

Jähne, B., Schmidt, M., & Rocholz, R. 2005c. Combined optical slope/height measurements of short<br />

wind waves: principle and calibration. Meas. Sci. Technol., 16, 1937–1944.<br />

Klar, M. 2005. Design of an endoscopic 3-D Particle-Tracking Velocimetry system and its application<br />

in flow measurements within a gravel layer. Ph.D. thesis, <strong>Universität</strong> Heidelberg.<br />

Liss, P. S., & Merlivat, L. 1986. Air-sea gas exchange rates: introduction and synthesis. Pages 113–127<br />

of: Buat-Menard, P. (ed), The Role of Air-Sea Exchange in Geochemical Cycling. Dordrecht, The<br />

Netherlands: Reidel.<br />

Nielsen, R. 2004. Hochgenaue Messung der Schmidtzahlabhängigkeit des Gasaustausches an einer<br />

wind- und wellenbewegten Wasseroberfläche. Ph.D. thesis, <strong>Universität</strong> Heidelberg.<br />

Rocholz, R. 2005. Bildgebendes System zur simultanen Neigungs- und Höhenmessung an kleinskaligen<br />

Wind-Wasser-Wellen. diploma thesis, <strong>Universität</strong> Heidelberg.<br />

Schimpf, U., Garbe, C. S., & Jähne, B. 2004. Investigation of transport processes across the seasurface<br />

microlayer by infrared imagery. Journal of Geophysical Research, C8(109). C08S13,<br />

doi:10.1029/2003JC001803.<br />

Schwarz, T. 2005. Development of a depth resolving boundary layer visualization for gas exchange at<br />

free water surfaces. diploma thesis, <strong>Universität</strong> Heidelberg.<br />

Wanninkhof, R. 1992. Relationship between wind speed and gas exchange over the ocean. J. Gephys.<br />

Res., 97, 7373–7382.<br />

Zappa, C. J., Asher, W. E., Jessup, A. T., Klinke, J., & Long, S. R. 2001. Effect of microscale wave<br />

breaking on air-water gas transfer. Pages 23–29 of: Donelan, M. A., Drennan, W. M., Saltzman,<br />

E. S., & Wanninkhof, R. (eds), Gas Transfer at Water Surfaces. Geophysical Monograph, vol. 127.<br />

Washington, DC: American Geophysical Union.<br />

Zhang, X., & Garbe, C. S. 2004. Studying dynamical processes of air-sea exchanges with air-water inerface<br />

image techniques. Chap. 3, pages 57–88 of: Recent Research Developments in Fluid Dynamics,<br />

vol. 5. Transworld Research Network.


Forschungsstelle “Radiometrie” of<br />

the Heidelberger Akademie der<br />

Wissenschaften<br />

6.1 Radiometric Dating of Water and Sediments . . . . . . . . . . . . . . . . 187<br />

185


6.1. RADIOMETRIC DATING OF WATER AND SEDIMENTS 187<br />

6.1 Radiometric Dating of Water and Sediments<br />

The Forschungsstelle is an independent research unit funded by the Heidelberger Akademie der Wissenschaften.<br />

Funding began in the year 1958 and will run until the end of 2010.<br />

Personnel :<br />

Prof. Dr. Augusto Mangini<br />

Dr. Bernd Kromer<br />

Dr. Marcus Christl<br />

Dr. Denis Scholz<br />

René Eichstätter, Technician<br />

Maleen Gillmann, Technician<br />

Sebastian Welk, Technician<br />

Karoline Thomas, Secretary<br />

Additional funding from the DFG, BMBF and EU (CarboEurope-IP):<br />

Scientists: Pablo Verdes, Marcus Christl, Denis Scholz, Andrea Schröder-Ritzrau, Sahra Talamo,<br />

Michael Friedrich,<br />

PhD-students: Frank Bernsdorff, Holger Braun, Nicolas Latuske, Jörg Lippold, Marga-rita Koroleva,<br />

Ingmar Unkel,<br />

Technicians: Helga Baus, Maleen Gillmann, Sabine Kühr, Eva Gier and 4 student assistants<br />

Master-students: Kerstin Bohn, Daniel Schimpf, Boris Schulze, Nicole Vollweiler, Patrick Wenderoth<br />

The task of the Forschungsstelle ”Radiometrie”of the Heidelberger Akademie der Wissenschaften is<br />

the dating and interpretation of climate archives. The research unit consists of two groups, the 14 C<br />

Lab (Bernd Kromer) and the Th/U-Lab (Augusto Mangini).<br />

14 C Lab The focus of the 14 C Lab are highly precise 14 C-dating and the construction of a calibration<br />

curve for radiocarbon that reaches far back into the last Glacial. Furthermore this Lab delivers 14 Cdatings<br />

for several archeological groups.<br />

Methods We use both the conventional gas-counting technique and AMS. The gas counters were<br />

developed to highest precision (better than 2 �). For AMS we prepare graphite targets, to be<br />

measured at one of the European AMS facilities.<br />

Extension of tree-ring based 14 C calibration into the Late Glacial In collaboration with<br />

the tree-ring laboratories of the University Stuttgart-Hohenheim and the University of Zürich/WSL<br />

Birmensdorf we extend the tree-ring based 14 C calibration into the past. Presently, the absolutely<br />

(annually) dated oak and pine chronology starts at 12.400 years BP (before AD 1950) [Friedrich et<br />

al., 2004; Reimer et al. 2004]. In the Late Glacial two independent chronologies were built in the two<br />

tree-ring labs, assisted by numerous 14 C predating in our laboratory [Kromer et al., 2004; Schaub et<br />

al., 2005]. Based on a comparison to the marine 14 C of [Hughen et al., 2004] the chronologies cover<br />

the mid-Bølling, all of the Allerød and the initial 150 years of Younger Dryas (ca. 14,100 to 12,800<br />

cal BP). The trees were recovered from gravel pits at the Danube river and its tributaries, the lignite<br />

area south-east of Berlin, and construction sites in Zürich. Beyond the range of these chronologies we<br />

assembled several floating 14 C sections from trees found in Northern Italy and Romania.<br />

The 14 C data sets are evaluated to infer solar activity variability [Bond et al., 2001; Solanki et al.<br />

2004, Usoskin et al., 2005] as well as ocean thermohaline circulation changes. Combined with 10 Be<br />

time series from Greenland they may serve to link tree-ring and ice-core time-scales. From dendroclimatological<br />

parameters of tree-rings, such as ring-widths, frost damage and growth patterns climate<br />

anomalies can be reconstructed.<br />

14 C dating, archaeology and geosciences We maintain extensive collaborations with archaeologists<br />

to date key sites, such as Troy [Kromer et al. 2002] or the Nasca sites in Peru [Eitel et al.<br />

2005], and to anchor floating tree-ring sections by 14 C wiggle-matching to the absolute scale. In the<br />

’Roman Gap Project’ (http://www.arts.cornell.edu/dendro/2004News/ADP2004.html) we assist in<br />

the extension of the Eastern Mediterranean chronologies into the first millennium AD, to link the<br />

absolute part to the 2300-year long Bronze Age chronology [Manning et al., 2003]. The date of the<br />

eruption of Thera remains a crucial and still controversial time marker of the Late Bronze Age in the<br />

Eastern Mediterranean. In long-standing collaborations with colleagues in archaeology we contribute<br />

to a high-precision 14 C date of this event [Manning et al., 2001].


188 CHAPTER 6. FORSCHUNGSSTELLE “RADIOMETRIE”<br />

14 C in the present-day carbon cycle The present-day 14 C level is largely determined by the<br />

re-equilibration of the atmosphere following strong 14 C input during the bomb testing up to 1962,<br />

and the dilution of the natural 14 C level by anthropogenic, 14 C free, CO2 emissions (see contribution<br />

by I. Levin in this report). In our laboratory continuous 14 C times series from several sites around<br />

the globe have been measured up to today, now covering more than 40 years [Levin & Kromer, 2004].<br />

Recently, 14 C has become an important marker to determine the ratio of fossil to present-day sources<br />

of carbon, e.g. in the emissions trading. Here we are involved in pilot studies to establish legislative<br />

procedures.<br />

Th/U-Lab The Th/U-Lab works on continental archives, such as speleothems and travertines, as<br />

well as on marine samples, such as deep sea sediments, Mn-nodules and corals.<br />

One principal focus is the determination of the natural variations of Holocene and Late Pleistocene<br />

climate using the stable isotopic composition of speleothems. Furthermore, we determine the magnitude,<br />

timing, and duration of past sea level fluctuations from the position and age of fossil coral reefs<br />

as well as the intensity of the Earths magnetic field during the past 350,000 years from 10 Berecords.<br />

These studies deliver a precise time scale for the variations of past climate. This is a basic requirement<br />

for the understanding of the causal relationships and the complex interplay between the forcing and<br />

feedback mechanisms in the climate system during the past 350,000 years and during the Holocene. We<br />

work in close cooperation with climate modelers from Hamburg and Berlin in the DEKLIM program<br />

(through 5/2006). With modelers from Potsdam we apply their CLIMBER2 model to study the<br />

abrupt climate changes that occurred during the Last Glacial (Dansgaard/Oeschger events).<br />

Methods We use dating methods, relying on the disequilibrium of the natural decay chains (TIMS-<br />

230 Th/U and 231 Pa/U). In addition, we use the decay of 10 Be, a radioactive product of cosmic rays.<br />

Speleothems, an archive of paleoclimate Speleothems are an excellent climate archive because<br />

they can be dated very precisely with the Th/U method. Stable isotope signals recorded in these<br />

stalagmites can be measured at a resolution of 100 µm and hence provide a climate signal of one-yearresolution.<br />

Most isotope signals in stalagmites display significant kinetic effects. These kinetic signals have been<br />

related to the intensity of precipitation within the last ten years. For example, periods of enhanced<br />

kinetic were ascribed to periods of less intense precipitation in speleothems from Oman and from<br />

Central Germany [Burns et al.,2002; Fleitmann et al., 2003; Neff et al., 2001; Niggemann et al,2003].<br />

The combination of this high resolution proxy for precipitation and the precise Th/U dating lead to<br />

a number of internationally regarded publications. For example, we found a very good correlation<br />

between the intensity of precipitation in Oman and the intensity of solar irradiation [Neff, 2001].<br />

This relationship has been confirmed by a number of following studies [e.g. Holzkämper et al., 2004;<br />

Mangini et al., 2005].<br />

In November 2005 we were granted by the DFG for a Forschergruppe (www.fg-Daphne.de) to study the<br />

basic processes affecting speleothem formation as well as the isotopic and the chemical signals. These<br />

studies will establish and improve the applicability of speleothems as archives for past precipitation<br />

and temperature. The DAPHNE project is funded for the next three years, with an option for funding<br />

for three additional years. We will work in close collaboration with groups from Bochum, Trento (Italy)<br />

and Innsbruck (Austria).<br />

Reconstruction of Sea level from fossil corals Reconstructions of past sea level allow to determine<br />

the magnitude, timing and duration of interglacial periods. which are essential for the understanding<br />

of the causal relationships and the complex interplay between the forcing and feedback<br />

mechanisms in the climate system.<br />

Some reef coral genera grow in upper 5m below sea surface only and record past sea level fluctuations.<br />

Thus, the determination of accurate U-series ages provides a direct method for sea level reconstruction.<br />

Unfortunately, many fossil reef corals show clear evidence for post-depositional open-system behaviour.<br />

There-fore, conventional Th/U-ages obtained from such corals cannot be considered as strictly reliable.<br />

We dealt with this problem (i) by identifying corals that have not been altered [Scholz and Mangini,<br />

in press] and (ii) by developing an appropriate correction technique [Scholz et al., 2004]. The results<br />

enabled to reconstruct sea level during Marine Isotope Substage 6.5 (∼175,000 years before present).<br />

The intensity of the Earth’s magnetic field in the past Accumulating evidence suggests that<br />

solar activity is responsible for at least some climatic variability. These include correlations between


6.1. RADIOMETRIC DATING OF WATER AND SEDIMENTS 189<br />

solar activity and either direct climatic variables or indirect climate proxies over time scales ranging<br />

from days to millennia [Eddy, 1976; Labitzke & van Loon, 1992; Svensmark & Friis-Christensen, 1997;<br />

Soon et al., 1996, 2000; Beer et al., 2000; Hodell et al., 2001]. A very notable correlation was that<br />

obtained in our group in Heidelberg [Neff et al., 2001]. However, the climatic variability attributable<br />

to solar activity is larger than could be expected from the typical 0.1% changes in the solar irradiance<br />

observed over the decadal to centennial time scale [Beer et al., 2000; Soon et al., 2000]. Thus, an<br />

amplifier is required unless the sensitivity to changes in the radiative forcing is uncomfortably high.<br />

The first suggestion for an amplifier of solar activity was suggested by Ney [1959], who pointed out<br />

that if climate is sensitive to the amount of tropospheric ionization, it would be sensitive the intensity<br />

of the Earth’s magnetic field as well as to solar activity since the solar wind modulates the cosmic ray<br />

flux (CRF), and with it, the amount of tropospheric ionization.<br />

We are studying 10 Be in marine sediments to determine the timing and the intensity of the Earth’s<br />

magnetic field in the past. The cosmogenic nuclide 10 Be is mainly produced in the lower stratosphere<br />

by interaction of galactic cosmic rays with oxygen and nitrogen atoms, and its production is known<br />

to be strongly anti-correlated with the solar- and/or geomagnetic field strength. In addition, highly<br />

resolved profiles of 10 Be in marine sediments may be used to synchronize the marine to the ice core<br />

ones.<br />

Cooperations The Forschungsstelle Radiometrie of the Heidelberger Akademie der Wissenschaften<br />

cooperates in the following projects with these institutions.<br />

Germany: Research Centre Ocean Margins, University of Bremen; Geosciences, University of Trier;<br />

<strong>Institut</strong>e for Paleontology, University of Erlangen; <strong>Institut</strong>e of Mineralogy, University of Frankfurt<br />

a.M.; <strong>Institut</strong>e of Environmental Geochemistry, University of Heidelberg; Potsdam <strong>Institut</strong>e for Climate<br />

Impact Research, Potsdam; Alfred-Wegener <strong>Institut</strong>e, Bremerhaven; ICG-V, Research-Centre<br />

Jülich; Faculty of Natural Sciences, University of Hohenheim, Stuttgart<br />

Foreign Countries: Paul-Scheerer <strong>Institut</strong>, ETH-Zürich, Switzerland Geology and Paleontology, University<br />

of Innsbruck, Austria<br />

Publications<br />

Peer Reviewed Publications<br />

1. Braun [in press]<br />

2. Christl et al. [2004]<br />

3. Eitel et al. [2005]<br />

4. Felis et al. [2004]<br />

5. Fleitmann et al. [2004]<br />

6. Friedrich et al. [2004]<br />

7. Holzkämper et al. [2004]<br />

8. Holzkämper et al. [2005]<br />

9. Hughen et al. [2004a]<br />

10. Hughen et al. [2004b]<br />

11. Kromer et al. [2004]<br />

12. Levin & Kromer [2004]<br />

13. Mangini et al. [2005]<br />

14. McHargue & Donahue [2005]<br />

15. McManus et al. [2004]<br />

16. Reimer et al. [2004]<br />

17. Schaub et al. [2005]


190 CHAPTER 6. FORSCHUNGSSTELLE “RADIOMETRIE”<br />

18. Scholz et al. [2004]<br />

19. Solanski et al. [2004]<br />

20. Usoskin & Kromer [2005]<br />

21. Verdes et al. [in pressa]<br />

22. Verdes et al. [in pressb]<br />

23. Wurth et al. [2004]<br />

Other Publications<br />

1. Christl et al. [2005]<br />

2. Scholz & Mangini [in press]<br />

3. Schröder Ritzrau et al. [2005]<br />

4. Spötl et al. [2004]<br />

Doctoral Theses<br />

1. Scholz [2005]<br />

Diploma Theses<br />

1. Bohn [2005]<br />

2. Schimpf [2005]<br />

3. Schulze [2005]<br />

4. Wenderoth [2005]


6.1. RADIOMETRIC DATING OF WATER AND SEDIMENTS 191<br />

6.1.1 Reconstruction of the geomagnetic field strength over the past 300,000<br />

years derived from 10 Be data of deep sea sediments from the North<br />

and South Atlantic Ocean<br />

Participating scientists Frank Bernsdorff, M. Christl, P. Wenderoth, B. Schulze, A. Mangini, D.<br />

Wagenbach, G. Brey (Frankfurt), P. Kubik (Zürich)<br />

Abstract In this project we use the anti correlation between the 10 Be production in the Earth’s<br />

stratosphere via galactic cosmic rays and the strength of the geomagnetic field to determine its variation<br />

over a time period of 300,000 years. Two deep sea sediment cores (ODP) from the Atlantic<br />

Ocean, which act as 10 Be archives are investigated.<br />

Background The cosmogenic nuclide 10 Be is<br />

mainly produced in the lower stratosphere by interaction<br />

of galactic cosmic rays with oxygen and<br />

nitrogen atoms, and its production is known to<br />

be strongly anti-correlated with the solar- and/or<br />

geomagnetic field strength. After a short atmospheric<br />

residence time of about 1 year 10 Be is<br />

removed from this part of the atmosphere and<br />

deposited onto land, ice sheets and (mainly) the<br />

ocean surface. Therefore, it should be possible<br />

to extract a record of geomagnetic paleointensity<br />

(GPI) from depositional profiles of these radionuclides<br />

in marine, terrestrial and ice core archives.<br />

In this study we are investigating two deep sea<br />

sediment cores from the North and South Atlantic<br />

Ocean (ODP-Site 983 and ODP-Site 1089)<br />

for highly resolved 10 Be profiles. The application<br />

of a special correction procedure (involving uranium<br />

and thorium measurements) is indispensable<br />

to quantify the transport of 10 Be in the ocean, so<br />

that the global 10 Be-production can be extracted<br />

from marine records. Based on these profiles, a<br />

marine 10 Be stratigraphy will be developed that<br />

can be matched with 10 Be records from Greenland<br />

(GRIP, GISP II) and Antarctic (EPICA) ice cores.<br />

In particular, enhanced global 10 Be-production<br />

during geomagnetic events (Lachamp, Blake, Jamaica)<br />

can be used as global time marker for the<br />

synchronization of marine and ice core chronologies.<br />

Based on the 10 Be stratigraphy a record of<br />

relative paleointensity will be calculated independently<br />

from the magnetization data<br />

Funding DFG Schwerpunktprogramm: Antarktisforschung<br />

mit vergleichenden Untersuchungen<br />

in arktischen Eisgebieten (SPP 1158)<br />

Methods and results Besides the measurement<br />

of 10 Be in Zürich, we are implementing the<br />

new technique of ICPMS for the precise determination<br />

of thorium and uranium isotopes in sediments.<br />

During initial tests we analyzed a number<br />

of different standard solutions and deep sea<br />

sediment samples of known isotopic composition.<br />

First samples of ODP 983 sediments are presently<br />

studied.<br />

Outlook/Future work According to the goals<br />

of this project, the future work will mainly comprise<br />

10 Be measurements of the deep sea sediments<br />

from ODP site 983, its normalization to<br />

230 T hxs(0) and comparison to the data set of ODP<br />

site 1089 (South Atlantic).<br />

Main publication Christl et al. [2005]


192 CHAPTER 6. FORSCHUNGSSTELLE “RADIOMETRIE”<br />

6.1.2 Possible solar origin of the glacial 1,470-year climate cycle demonstrated<br />

in a coupled climate model<br />

Participating scientists H.Braun, M.Christl, A.Mangini, B.Kromer (AdW Heidelberg), K.Roth<br />

(IUP Heidelberg), S.Rahmstorf, A.Ganopolski (PIK Potsdam), C.Kubatzki (AWI Bremerhaven)<br />

Abstract It is shown that an intermediate-complexity climate model reproduces abrupt glacial<br />

warmings (Dansgaard-Oeschger events) with a spacing of 1470 years when forced by freshwater cycles<br />

of about 87 and 210 years, i.e. with periods close to known solar cycles. Thus, the glacial 1470-year<br />

climate cycle could be caused by the Sun despite the lack of a 1470-year solar period.<br />

Figure 6.1: Forcing and model response. The applied freshwater forcing (left panel, in mSv [1 Sv =<br />

106 m 3 /s]) is the sum of two sinusoidal cycles with periods of 210 years and 86.5 years, respectively.<br />

These periods are close to well-known solar cycles. In response to this forcing, the applied climate<br />

model can show abrupt warm events in Greenland (Dansgaard-Oeschger events) with a period of 1470<br />

years (right panel, in ◦ C). The dashed lines in both panels are spaced by 1470 years.<br />

Background Many paleoclimatic archives show<br />

a quasi-cycle of about 1470 years in the Last<br />

Glacial. This pattern is manifested in rapid<br />

climate shifts, the so-called Dansgaard-Oeschger<br />

(DO) events. To explain these, various concepts<br />

have been proposed, including internal oscillations<br />

in the climate system and external (e.g. solar)<br />

forcing. However, while pronounced solar cycles<br />

of about 87 and 210 years are well-known [Peristykh<br />

and Damon 2003, Wagner et al. 2001], a<br />

1470-year cycle has not been found [Stuiver and<br />

Braziunas 1993]. This has been considered as a<br />

main argument against solar origin of the glacial<br />

1470-year climate cycle.<br />

Funding This work was funded by the Heidelberg<br />

Academy of Sciences.<br />

Methods and results To test if the lack of<br />

a 1470-year solar cycle indeed argues against solar<br />

origin of the DO events, we used the climate<br />

system model CLIMBER-2 of the Potsdam <strong>Institut</strong>e<br />

for Climate Impact Research (PIK). In earlier<br />

simulations with the model, abrupt glacial warming<br />

events were already simulated which reproduce<br />

many features of the observed DO events<br />

[Ganopolski and Rahmstorf 2001, Ganopolski and<br />

Rahmstorf 2002]. In the model, DO events represent<br />

rapid transitions between a stadial (cold)<br />

and an interstadial (warm) mode of the North Atlantic<br />

thermohaline circulation (THC), triggered<br />

by a threshold process.<br />

In our model study, a freshwater forcing was applied<br />

which is the sum of two sinusoidal components<br />

with periods 1470/7 (=210) and 1470/17<br />

(about 86.5) years (left panel in figure 1). The amplitudes<br />

of both forcing components are small (10<br />

mSv, i.e 10.000 m 3 /s), that is, about 5 cm/year<br />

in the surface freshwater flux. Although the total<br />

forcing does not explicitly have a spectral component<br />

of 1470 years, it repeats with this period due<br />

to the combined effect of the applied cycles.<br />

The forcing can excite DO-like events in the North<br />

Atlantic region (right panel in 6.1). Within a large<br />

forcing-parameter range, these events are spaced<br />

by 1470 years. This timescale is robust when<br />

the phases, amplitudes, and periods of the two<br />

forcing cycles are changed over some range. If<br />

instead of two sinusoidal cycles a more realistic<br />

forcing is applied with spectral properties close<br />

to that observed in solar proxies, a regular 1470year<br />

model response is still found. The stability<br />

of the simulated 1470-year cycle results from two<br />

well-known properties of the THC: its long characteristic<br />

timescale, and the non-linearity (i.e. the<br />

threshold character) inherent in the transitions<br />

between the two modes of the THC. For Holocene<br />

conditions, DO events do not occur in the model.<br />

To conclude, our results show that the lack of<br />

a 1470-year solar cycle does not by itself argue<br />

against a solar origin of the glacial 1470-year climate<br />

cycle.<br />

Main publication Braun et al. [in press]


6.1. RADIOMETRIC DATING OF WATER AND SEDIMENTS 193<br />

6.1.3 Solar variability and rapid climate change on decadal to centennial<br />

scales<br />

Participating scientist Michael Friedrich (<strong>Universität</strong> Hohenheim), Bernd Kromer, Nicolas Latuske,<br />

Sabine Remmele (<strong>Universität</strong> Hohenheim), Gerd Schleser (Forschungszentrum Jülich)<br />

Abstract The relation between solar variability and climate variations in the Holocene was investigated.<br />

The heliomagnetic variations were derived from fluctuations of the production of 14 C,<br />

calculated from the atmospheric 14 C activity using a carbon box model. Statistical parameters obtained<br />

from tree ring widths were correlated with the 14 C production at two intervals of low solar<br />

activity where previously cooling in the North Atlantic has been documented. Generally only weak<br />

correlations were found, probably pointing to a low climate sensitivity of riverine oaks in the Holocene.<br />

Figure 6.2: Spectral features in the detrended ∆ 14 C data (upper curve); and band-pass-filtered ∆ 14 C.<br />

Center band-pass wavelength are of 88, 210, 500 and 950 years (top to bottom).<br />

Background The sun is the most important<br />

driving force in the climate system, but only little<br />

is know how the climate system reacts to changes<br />

of the solar magnetic activity on decadal to multicentennial<br />

scales. It is known that the Little Ice<br />

Age coincided with the decrease of solar activity<br />

in the Maunder Minimum (1645-1715) but the<br />

mechanism remains unclear. To investigate how<br />

the variation of the climate system responses to<br />

the variability of solar activity, we used the atmospheric<br />

14 C signal (∆ 14 C) recorded in tree rings<br />

as proxy of solar activity.<br />

In this study we investigated the variation of<br />

∆ 14 C changes in the time period of the Holocene<br />

on time scales from decades to centennial and<br />

correlated statistic parameters as calculated from<br />

tree rings with selected maxima of 14 C production<br />

(minima of solar activity).<br />

Funding Deutsches Klimaforschungsprogramm<br />

(DEKLIM)<br />

Methods and results The fluctuations in<br />

the 14 C production were calculated from the<br />

atmospheric 14 C (∆ 14 C) using a Oeschger-<br />

Siegenthaler-type box-diffusion model of the carbon<br />

cycle. Model experiments were done to investigate<br />

the influence of changes in diffusive deepocean<br />

ventilation, air-sea gas exchange rate and<br />

14 C production. Furthermore, the atmospheric<br />

14 C was spectrally analyzed with various methods<br />

(Singular Spectrum Analysis, Maximum Entropy<br />

Method and Multi Taper Method, Digital Filters<br />

(IIR) and Wavelets) to obtain solar variability periods<br />

(Fig. 6.2). Finally, statistical parameters of<br />

tree ring chronologies in southern Germany were<br />

calculated, and they were correlated to the 14 C<br />

production changes at intervals of low solar activity<br />

(∆ 14 C maximum).<br />

In two intervals of low solar activity, centered<br />

at 2800 BC and 800 BC, respectively, the treering<br />

parameters (derived from the ring widths) are<br />

weakly correlated with the 14 C production. The<br />

tree-ring parameters indicate that in these intervals<br />

the precipitation increased and the temperature<br />

decreased at times of solar minimum, pointing<br />

to a role of solar forcing of climate variability.<br />

Model experiments to explain instances and observed<br />

decrease of ∆ 14 C about 10 � over 20 years<br />

are compatible with an increase of the ocean circulation<br />

and gas exchange rate at a factor of 2 and<br />

a decrease at 25 % for the 14 C production.<br />

The results of spectral analysis ∆ 14 C are shown<br />

in Figure 6.2.<br />

Outlook/Future work none in this case<br />

Main publication in preparation


194 CHAPTER 6. FORSCHUNGSSTELLE “RADIOMETRIE”<br />

6.1.4 Establishment of a method for measuring 231 Pa in deep-sea sediments<br />

via ICP-MS<br />

Participating scientist Jörg Lippold, M. Christl, A. Mangini, G. Brey (Frankfurt).<br />

Abstract Using ICP-MS, the 231 Pa / 230 Th ratio of deep-sea sediments can be estimated more<br />

efficiently and precisely than by α-spectrometry. The measurement of the tracers 231 Pa and 230 Th<br />

allows a high resolution for paleoproductivity and ocean circulation studies on glacial to interglacial<br />

timescales.<br />

Background 231 Pa and 230 Th are natural radionuclides,<br />

which are continously produced in<br />

seawater by in situ decay of their dissolved progenitors<br />

234 U and 235 U. As a result, both are produced<br />

at a constant rate with an initial 231 Pa and<br />

230 Th activity ratio of 0.093. Variable 231 Pa and<br />

230 Th ratios in sediments indicate that both radionuclides<br />

follow different pathways of removal<br />

from the water column. The flux of 230 Th to<br />

the seafloor is nearly identical to its rate of production.<br />

In contrast, the longer oceanic residence<br />

time for dissolved 231 Pa due to lower particle reactivity<br />

allows a large scale diffusive transport over<br />

basin-wide distances prior to scavenging, resulting<br />

in its preferential removal in high particle flux<br />

regions.<br />

Particularly in the North Atlantic region radioisotope<br />

signals may be significantly influenced by<br />

changes in Ocean circulation. Up to now, the<br />

231 Pa and 230 Th-ratio is the best kinematic proxy<br />

to quantify the strength of the meridional overturning<br />

circulation. A high resolution study of<br />

the sedimentary 231 Pa and 230 Th-ratio showed<br />

that North Atlantic meridional overturning was<br />

highly variable, switching very fast from an offmode<br />

(during Heinrich Event H1) to almost modern<br />

conditions (Bølling-Allerød) during the past<br />

20 kyr. Thus, 231 Pa and 230 Th-data, that provide<br />

the best estimate of ocean circulation in the<br />

past, can be used as input for model calculations<br />

to quantify the transport of other tracers (e.g. 10<br />

Figure 6.3: Planktonic foraminifera δ 18 O (upper<br />

curve) plotted with sedimentary 231 Pa and<br />

230 Th (lower curve) against age, sediment core<br />

at 33 ◦ N, 57 ◦ W, [McManus et al., 2004].<br />

Be) in the North Atlantic Ocean. Because of the<br />

32.5 kyr half life of 231 Pa, this method is restricted<br />

to the last about 90 kyr [McManus et al., 2004],<br />

[Walter, 1998].<br />

Funding DFG Schwerpunktprogramm 527 and<br />

1158.<br />

Methods and results The accurate and precise<br />

determination of the very low 231 Pa content<br />

in marine sediments requires the application of<br />

a new analytical technique. ICP-MS is currently<br />

the most suitable analytical tool for high precision<br />

measurements of heavy isotope ratios. A cooperation<br />

with the <strong>Institut</strong>e of Mineralogy at the University<br />

of Frankfurt to develop the appropriate analytical<br />

techniques for the determination of Th/U,<br />

and Pa- isotope-ratios with Inductively Coupled<br />

Plasma Mass Spectrometry (ICP-MS) was initiated.<br />

Outlook/Future work In combination with<br />

published 231 Pa and 230 Th-data from the North<br />

Atlantic region, these records will help to greatly<br />

improve our understanding of past Ocean circulation<br />

in this region. Once established, the 231 Pa<br />

measurement method can be applied to further<br />

paleoclimate records, e.g. corals.<br />

Main publication in preparation


6.1. RADIOMETRIC DATING OF WATER AND SEDIMENTS 195<br />

6.1.5 Modelling of stable isotope records of stalagmites<br />

Participating scientist Christian Mühlinghaus, D. Scholz, D. Schimpf, A. Mangini<br />

Abstract Speleothems can be precisely dated with the Th/U method. Climate variations are<br />

recorded in the δ 18 O and δ 13 C of their calcium carbonate. We are developing models to evaluate<br />

drip rates (and other parameters) at the time of growth from the isotopic enrichment of δ 13 C from<br />

the stable isotope records of close-by stalagmites.<br />

1200<br />

1000<br />

Tropfabstand dT [s]<br />

800<br />

600<br />

400<br />

200<br />

T: 6.5<br />

Ma2<br />

0<br />

0 0.5 1 1.5 2 2.5<br />

Alter [ka]<br />

3 3.5 4 4.5<br />

Figure 6.4: Drip rate of stalagmites from Chile calculated by the I model.<br />

Background The isotopic composition of stalagmites<br />

growing under kinetic conditions has<br />

barely been interpretable. Only under equilibrium<br />

formation a temperature signal of δ 18 O could<br />

be deduced. Understanding of the process of kinetic<br />

fractionation, would deliver information on<br />

the drip rate and, therefore, precipitation.<br />

Funding Diplomarbeit, therefore ”not applicable”<br />

Methods and results Drip rate, cave temperature,<br />

calcium concentration, the isotopic composition<br />

of the drop as well as mixing parameters<br />

affect the stable isotope composition of<br />

speleothems.<br />

Three different models were developed to determine<br />

past drip rates. And the sensitivity to these<br />

parameters was tested.<br />

A-Model The age-height-model is based upon<br />

the considerations of W. Dreybrodt [1999] and G.<br />

Kaufmann [2003]. Through a comparison of ages<br />

and heights of different growth layers, drip rates,<br />

calcium concentration and mixing parameter can<br />

be obtained. Hence, the outer form of a stalagmite<br />

can be modeled by given parameters.<br />

I-Model The isotopic model is based on isotopic<br />

enrichment of δ 13 C along the growth axis of<br />

Ma1<br />

a stalagmite due to kinetic fractionation. By comparing<br />

the intersections of modeled drip rate and<br />

isotopic curves of two close-by stalagmites, drip<br />

rates, the isotopic composition of the drop and the<br />

mixing parameter can be determined. Calibrating<br />

the A-Model with these results yields more<br />

information about the calcium concentration of<br />

the drop. This has been done for two close-by<br />

stalagmites from a cave in South Chile.<br />

H-Model The Hendy-Model uses measured<br />

Hendy tests to determine drip rates more accurately.<br />

It is similar to the I-Model, but it is coupled<br />

with an additional box model. Using isotopic<br />

fractionation, one can obtain the range of<br />

drip rate and temperature from the isotopic enrichment<br />

along a growth layer. The correlation<br />

between the drip rate and ∆δ 18 O/∆δ 13 C was constructed.<br />

Outlook/Future work Aim of this work is to<br />

correct for the kinetic effect using the slope of<br />

∆δ 18 O/∆δ 13 C and to determine temperatures in<br />

the cave from the δ 18 O signals of speleothems.<br />

These models are used in the DFG-Project<br />

Forschergruppe 668 (www.FG-daphne.de).<br />

Main publication in preparation


196 CHAPTER 6. FORSCHUNGSSTELLE “RADIOMETRIE”<br />

6.1.6 Reconstruction of the 10 Be-production based on deep sea sediments<br />

from the North Atlantic<br />

Participating scientist Boris Schulze, M. Christl, F. Bernsdorff, A. Mangini, D. Wagenbach, P.<br />

W. Kubik (Zürich)<br />

Abstract The 10 Be-production is inversely related with the Earth‘s magnetic field strength. A<br />

highly resolved record of 10 Be-production is produced based on highly accumulating deep sea sediments<br />

from Bermuda Rise. The data support the idea of using 10 Be as a global matching-tool and as<br />

a proxy for geomagnetic paleointensity.<br />

Figure 6.5: 10 Be deposition rate, transport corrected by 230 Th-normalization. Compared are data from<br />

ODP Sites 1063 (North Atlantik; red) and 1089 (South Atlantic; blue).<br />

Background Cosmogenic 10 Be is produced by<br />

the interaction of galactic cosmic rays with oxygen<br />

and nitrogen atoms in the upper atmosphere<br />

of the Earth. Thus, 10 Be-production is inversely<br />

related with the Earth‘s magnetic field strength.<br />

After different processes of transport, the variations<br />

of the 10 Be-production eventually are conserved<br />

as varying 10 Be-deposition fluxes in different<br />

archives (ice cores, marine and terrestrial<br />

sediments). Knowing the past production rate<br />

of 10 Be, it should be possible to synchronize<br />

chronologies of different archives by comparison<br />

of the reconstructed 10 Be-deposition fluxes.<br />

Funding DFG Schwerpunktprogramm: Antarktisforschung<br />

mit vergleichenden Untersuchungen<br />

in arktischen Gebieten (SPP 1158)<br />

Methods and results A high-resolution record<br />

of 10 Be-production is produced based on highly<br />

accumulating deep sea sediments from Bermuda<br />

Rise (ODP Site 1063). To correct for marine<br />

transport signals, the 230 T hexcess normalisation<br />

technique is applied. The 10 Be -concentration<br />

(measured at the ETH-Zürich) and the activity of<br />

Th/U-isotopes (by alpha-spectroscopy) were determined<br />

in sediments of the past 100 kyr. The<br />

comparison of the 230 T h-normalized 10 Be-flux at<br />

Site 1063 with other records ( 10 Be-fluxes, atmospheric<br />

∆ 14 C, and paleointensity) revealed a very<br />

good interhemispheric correlation. Thus, the results<br />

of this work strongly support the idea of using<br />

10 Be as a global matching-tool for the synchronisation<br />

of marine, terrestrial, and ice-core<br />

chronologies and as a proxy for geomagnetic paleointensity.<br />

Outlook/Future work The 10 Be and U/Thdataset<br />

of the deep sea sediments from ODP Site<br />

1063 will be further expanded and compared to<br />

the data from ODP Sites 983 (North Atlantic) and<br />

1089 (South Atlantic).<br />

Main publication Schulze [2005]; Christl et al.<br />

[2005]


6.1. RADIOMETRIC DATING OF WATER AND SEDIMENTS 197<br />

6.1.7 U/Th dating of deep-water corals from the North Atlantic<br />

Participating scientist Andrea Schröder-Ritzrau, A. Mangini, A. Freiwald (Tübingen), G. Hoffman<br />

(Zürich)<br />

Abstract Coupled uranium-series and radiocarbon measurements on deep-water corals are a proxy<br />

to estimate intermediate water ages. 17 intermediate water ages were estimated on deep-water corals<br />

from the eastern North Atlantic. These data give strong evidence for periodic reduced ventilation in<br />

the North Atlantic during the LGM/Holocene transition.<br />

600<br />

400<br />

� 14 C ‰<br />

200<br />

0<br />

� C Cariaco Basin; Hughen et al. 2004<br />

14<br />

� 14<br />

C model/atm; Laj et al. 2002<br />

� 14<br />

C atm INTCAL; Reimer et al. 2004<br />

� 14<br />

C marin INTCAL; Hughen et al. 2004<br />

-200<br />

0 4000 8000 12000 16000 20000 24000<br />

age (years BP)<br />

Figure 6.6: ∆ 14 Cintermediate water (red data points) compared to various ∆ 14 C records and models (see<br />

references in the Fig.). Data are plotted without error bars for clarity - except for the deep-water coral<br />

data.<br />

Background Thermohaline circulation in the<br />

world ocean has a major influence on climate.<br />

Hence, changes of thermohaline circulation and<br />

water mass distribution especially in the North<br />

Atlantic during climate transitions are of major<br />

interest for paleoceanographic and climatic reconstructions.<br />

It is suggested that at terminations<br />

the intermediate water has a larger component of<br />

poorly ventilated SSW (Southern Source Water)<br />

compared to interglacials and full glacials.<br />

The 14 C/ 12 C ratio of dissolved inorganic carbon<br />

is a powerful tracer for reconstructing the<br />

pathways of deep- and intermediate water in the<br />

ocean. Coupled AMS- 14 C- and Th/U- (TIMS)<br />

measurements on coral carbonate, deliver a snapshot<br />

of the 14 C-concentration of deep- or intermediate<br />

water at the time and place the coral lived<br />

[Mangini et al. 1998].<br />

Funding DFG and EU<br />

Methods and results Intermediate water ages<br />

were calculated via the method of 14 C projection<br />

ages [Adkins and Boyle, 1997]. Radiocarbon<br />

dates (measured at the ETH-Zurich and at<br />

the Leibniz-Laboratory in Kiel) and uranium series<br />

ages (via TIMS in HD) were used to calculate<br />

the ∆ 14 Cintermediate water of the former sur-<br />

rounding intermediate water the coral lived in.<br />

Assuming closed system radiocarbon decay and<br />

no further exchange with atmospheric radiocarbon,<br />

the calculated ∆ 14 Cintermediate water of the<br />

coral (Fig. 6.6) can be backtracked to the crossover-point<br />

with the (∆ 14 C past/atm) [Reimer et al.,<br />

2004]. This ratio (∆ 14 C past/coral) is the ratio of<br />

the water that had equilibrated with the past atmosphere.<br />

This value was applied in the equation<br />

for the ventilation age [Mangini et al., 1998] where<br />

non-reservoir-corrected ventilation ages (intermediate<br />

water ages) are determined.<br />

A total of 69 deep-water corals were investigated<br />

and 17 intermediate water ages were calculated.<br />

Our data document short periods of reduced conveyor<br />

circulation associated with increasing influence<br />

of SSW at intermediate water depth at the<br />

end of Heinrich I and the end of the Younger Dryas<br />

event. These periods are associated with meltwater<br />

discharge (MPIA and B). A similar event in<br />

the early Holocene has to be verified.<br />

Outlook/Future work none in this case, the<br />

project is finished<br />

Main publication Schröder-Ritzrau et al.<br />

[2003]; Schröder-Ritzrau et al. [2005]


198 CHAPTER 6. FORSCHUNGSSTELLE “RADIOMETRIE”<br />

6.1.8 Isochron dating of fossil reef corals and the reconstruction of past<br />

sea level fluctuations<br />

Participating scientist Denis Scholz, A. Mangini, K. Bohn, T. Felis (Bremen), D. Meischner<br />

(Göttingen)<br />

Abstract We developed an isochron dating approach that enables to derive reliable ages for fossil<br />

reef corals that cannot be dated by the conventional Th/U-method. Isochron dating was applied to<br />

Porites corals from Aqaba and Baja California. In addition, we reconstructed magnitude,timing, and<br />

duration of the Marine Isotope Substage (MIS) 6.5 ( 175,000 years before present) sea level peak by<br />

U-series dating of fossil Acropora palmata corals from Barbados.<br />

Figure 6.7: Isochron dating of coral AQB 3A from<br />

Aqaba. The isochron age is calculated from the intersection<br />

point, the age error is estimated from<br />

the intersection points of the confidence bands.<br />

Background Reconstructions of past sea level<br />

fluctuations allow to determine the magnitude,<br />

timing and duration of glacial/interglacial periods.<br />

This is essential for the understanding of the<br />

causal relationships and the complex interplay between<br />

the forcing and feedback mechanisms in the<br />

climate system.<br />

Some reef coral genera grow in upper 5m below<br />

sea surface only and record past sea level fluctuations.<br />

Thus, the determination of accurate<br />

U-series ages provides a direct method for sea<br />

level reconstruction. Unfortunately, many fossil<br />

reef corals show elevated ( 234 U/ 238 U) activity ratios<br />

which are clear evidence for post-depositional<br />

open-system behaviour. Therefore, conventional<br />

Th/U-ages obtained from such corals cannot be<br />

considered as strictly reliable. There are two possibilities<br />

to deal with this problem: (i) to identify<br />

corals that have not been altered and (ii)<br />

to develop and apply appropriate correction techniques.<br />

Funding BMBF (DEKLIM project)<br />

Methods and results We analysed five fossil<br />

Porites corals from Aqaba, Jordan, by<br />

thermal ionisation mass spectrometry (TIMS).<br />

( 234 U/ 238 U) and ( 230 T h/ 238 U) activity ratios of<br />

Figure 6.8: Sea level reconstruction for MIS 6.5.<br />

Black squares are our coral data from Barbados.<br />

Red and yellow symbols are coral data from other<br />

studies, straight curves are based on oxygen isotopes.<br />

different sub-samples from one coral specimen<br />

show a high linear correlation (Fig. 6.7). This<br />

can be explained by a model assuming different<br />

degree of U addition and subsequent loss for different<br />

sub-samples. The model predicts that the<br />

true coral age can be calculated from the intersection<br />

point of the isochron with the seawater<br />

evolution curve (Fig. 6.7). Isochron dating was<br />

also successfully applied to corals from Baja California,<br />

Mexico [Bohn, 2005].<br />

Detailed investigation of Acropora palmata corals<br />

from Barbados, West Indies, showed that<br />

these corals suffered U-redistribution [Scholz and<br />

Mangini, in press]. Thus, isochron dating cannot<br />

be applied. Careful selection of reliable Th/Uages<br />

by application of strict reliability criteria<br />

suggests that MIS 6.5 sea level ranged from -<br />

50±11 to -47±11 m relative to present sea level<br />

between 176,100±2,800 and 168,900±1,400 years<br />

before present (Fig. 6.8). At present, this reconstruction<br />

is one of the most accurate for MIS 6.5.<br />

Outlook/Future work publication of results<br />

Main publication Scholz et al. [2004], Felis et<br />

al. [2004], Scholz [2005], Bohn [2005], Scholz and<br />

Mangini [in press]


6.1. RADIOMETRIC DATING OF WATER AND SEDIMENTS 199<br />

6.1.9 Dating and interpretation of the carbon and oxygen isotopes of two<br />

Holocene stalagmites from the South of Chile (Patagonia)<br />

Participating scientist Daniel Schimpf, C. Mühlinghaus, D. Scholz, A. Schröder-Ritzrau, A.<br />

Mangini, R. Kilian (Trier), C. Spötl (Innsbruck)<br />

Abstract Two Holocene stalagmites (MA-1 and MA-2) from the Marcelo-Arevalo cave, which is<br />

located in the South of Chile (53 ◦ S) in the vicinity of the Pacific coast, were dated with the 230 T h/ 234 U<br />

method and analyzed with respect to their oxygen and carbon isotopes. We find that the Westwind<br />

drift, which controls precipitation, is strongly influenced by the El Nino Southern Oscillation.<br />

age (ka BP)<br />

5<br />

4<br />

3<br />

2<br />

1<br />

Stalagmite MA-1<br />

Akima fit<br />

0<br />

0 50 100 150 200 250<br />

distance from top (mm)<br />

Background For the first time stalagmites<br />

from a cave of the southernmost Andes were analyzed<br />

at high resolution. The intensity of precipitation<br />

at this location reflects the shifts of the<br />

position of the Westwind drift.<br />

Funding Diploma thesis, therefore not applicable.<br />

Methods and results The 230 T h/ 234 U dating<br />

method was used to establish a depth-age model<br />

for the two stalagmites (MA-1 and MA-2). The<br />

measurements were performed with a Thermal<br />

Ionization Mass Spectrometer (TIMS). Figure 6.9<br />

shows the depth-age model for stalagmite MA-1<br />

including all reliable data points. An Akima fit<br />

was implemented to get a continuous depth-age<br />

Figure 6.9: Depth-age model of stalagmite MA-1.<br />

relation. It shows an almost linear relation between<br />

age and depth.<br />

The comparison of the dated δ 13 C and δ 18 O profiles<br />

with a record of the ENSO intensity, derived<br />

from a sediment record off the coast of Peru, reveals<br />

that the ENSO strongly influenced the intensity<br />

of precipitation, probably causing North-<br />

South-shifts of the Southern Westerlies.<br />

Outlook/Future work Further stalagmites<br />

from the Marcelo-Arevalo cave will be analysed.<br />

The stable isotope profiles are modeled by C.<br />

Mühlinghaus. We have applied for a DFG -<br />

Project to continue this study.<br />

Main publication Schimpf [2005]


200 CHAPTER 6. FORSCHUNGSSTELLE “RADIOMETRIE”<br />

6.1.10 Chronostratigraphy of the Nasca culture and palaeoclimate reconstruction<br />

of the Palpa region (Peru) by AMS- 14 C dating<br />

Participating scientist Ingmar Unkel, B. Kromer, G. Wagner, B. Eitel, L. Wacker (Zürich)<br />

Abstract Research on the enigmatic Nasca culture in South-Peru is driven by two major questions:<br />

when did the Nasca people live, and did changing climate have an influence on the rise and fall of this<br />

Pre-Columbian civilisation? AMS- 14 C-dating and investigations in an multi-disciplinary project help<br />

to get the first answers.<br />

Figure 6.10: (left) Preparation line for AMS- 14 C-targets built at the IUP during this project. (right)<br />

A trapezoid, one of the famous Nasca-geoglyphs, in the research area near Palpa (S-Peru).<br />

Background The chronology of the Nasca culture,<br />

which created the world famous geoglyphs<br />

(giant diagrams etched into the desert ground)<br />

and spanning from approximately 200 BC to 600<br />

AD, in the plain between the Peruvian Andes and<br />

the Pacific Ocean, is presently based almost exclusively<br />

on a ceramic typology without any extensive<br />

chronometric dating. An absolute chronology<br />

of this culture had to be created via radiocarbon<br />

dating on organic samples from settlement and<br />

tomb relics as well as on organic material derived<br />

from geoglyph sites in the Nasca/Palpa region.<br />

Furthermore, the question is under investigation,<br />

if changing climate had influence on the rise and<br />

fall of the Pre-Columbian cultures in South-Peru.<br />

Funding BMBF focus programme ”New technologies<br />

in humanities”, project No. 03WAX3VP<br />

- title: ”Nasca: development and adaptation of<br />

archaeometric techniques for the investigation of<br />

the cultural history of the Palpa region, S-Peru”<br />

Methods and results The main focus of the<br />

archaeological investigations was on the Nascaperiod<br />

settlement centres near Palpa, Los Molinos<br />

und La Mua. In co-operation with the geomorphological<br />

investigations within the parent<br />

project, palaeoclimatic reconstruction of the re-<br />

spective region was undertaken. The material to<br />

be dated consisted mainly of loess molluscs and<br />

charred plant remains, sampled from river terraces<br />

and debris flows which originated in more humid<br />

phases in this presently hyper-arid area.<br />

During the course of the project a semi-automated<br />

AMS-target preparation line was built in the<br />

radiocarbon laboratory. Using AMS (Accelerator<br />

Mass Spectrometry), dating of extremely<br />

small amounts of archaeological material is possible.<br />

For the first time in Peruvian archaeology<br />

straw fragments found within adobes (clay<br />

bricks), which do not provide a sufficient amount<br />

of material for conventional measurement, have<br />

been dated.<br />

The dating of the samples appears to confirm so<br />

far the archaeological timeframe of the Nasca culture.<br />

The chronology will be completed and statistically<br />

analysed towards the end of this year.<br />

Some surprising new evidence of climate change<br />

has been found in the studies of the river sediments,<br />

showing a pronounced wet phase from 15 th<br />

to 17 th century in that region. The analysis is still<br />

in progress.<br />

Outlook/Future work none in this case<br />

Main publication in preparation


6.1. RADIOMETRIC DATING OF WATER AND SEDIMENTS 201<br />

6.1.11 Nonlinear time-series analysis of nonstationary signals<br />

Participating scientists Pablo Verdes, A. Mangini<br />

Abstract The purpose of my research is to develop new tools for the analysis of nonstationary<br />

complex systems. I explore them using a natural decomposition into intrinsic dynamics and external<br />

component, using a previously developed technique to estimate the latter from measured data. In<br />

particular, I investigate how modeling and forecasting can be improved in this framework.<br />

Background One of the main goals of Physics<br />

has always been prediction. The most satisfactory<br />

situation arises when the system of interest<br />

can be completely understood and modeled from<br />

first principles, so that its equations of motion<br />

can be derived and solved for all times. However,<br />

real-world dynamical systems have often so many<br />

degrees of freedom that the traditional approach<br />

proves intractable. In such a case, an alternative<br />

path is to measure the evolution of any given<br />

system property by recording time series, which<br />

are a set of observations collected at regular intervals<br />

of time, and then recurr to the theory of<br />

time-series analysis. The vast literature on this<br />

subject mostly rely on the condition of stationarity,<br />

because a solid mathematical foundation can<br />

be built in this case. As a result, nonstationary<br />

time-series analysis is an almost unexplored<br />

branch of science. However, the stationarity condition<br />

is very stringent because most real-world<br />

time series have some degree of nonstationarity<br />

due to external perturbations acting on the observed<br />

system.<br />

Funding Alexander von Humboldt postdoctoral<br />

fellowship.<br />

Methods and results I have investigated the<br />

problem of modeling and forecasting of nonstationary<br />

time series. More precisely, I have studied<br />

an over-embedding method that constitutes a general<br />

framework for modeling nonstationary systems,<br />

basically enlarging the standard time-delay<br />

embedding space by inclusion of the unknown slow<br />

driving signal. I have developed a variant in which<br />

this external driving force can be estimated simultaneously<br />

with the intrinsic stationary dynamics.<br />

This method is general and can be implemented<br />

with any modeling tool; using in particular artificial<br />

neural networks, I have found that it is highly<br />

efficient both on synthetic and real-world time series.<br />

In particular, in noiseless artificial cases this<br />

approach is more than one order of magnitude<br />

better than the second best method. As a realworld<br />

application, I have considered the problem<br />

of modeling the sunspot number record. In this<br />

case a 30% error reduction was obtained, which is<br />

a remarkable number within the vast literature on<br />

this benchmark, particularly for an already very<br />

competitive modeling methodology like ensembles<br />

of artificial neural networks. In the case of nstep-ahead<br />

predictions, this approach also leads<br />

to much more accurate results and longer prediction<br />

horizons than other existing overembedding<br />

methods in the literature.<br />

We have also studied a time series of temperatures<br />

in the Central Alps during the past 2000 years reconstructed<br />

from a δ 18 O stalagmite record. The<br />

isotopic composition of this stalagmite could be<br />

precisely dated and translated into a highlyresolved<br />

record of temperature during the last 2<br />

millenia. The variability of this time series was<br />

analysed and compared to other reconstructions<br />

of past temperatures in the literature, and the role<br />

of the solar signal as a possible driver of its dynamics<br />

was assessed in comparison with carbon<br />

dioxide. The fractions of temperature variance<br />

that are explained by each of these forcing factors<br />

were analysed in a nonlinear framework, by studying<br />

the relevance of the solar and greenhouse gas<br />

inputs in a feed-forward neural network model of<br />

the temperature behaviour.<br />

I have also participated in a time series prediction<br />

competition organised by the International Joint<br />

Conference on Neural Networks. The goal of this<br />

competition was to provide a new benchmark for<br />

the problem of time series prediction and to compare<br />

the different methods or models that can be<br />

used for the prediction. An artificial time series<br />

with 5000 data was given and, within those, 100<br />

values were missing and had to be predicted. Selected<br />

papers were considered for publication in<br />

Neurocomputing.<br />

Main publications Verdes et al. [pub.];<br />

Mangini et al. [2005]; Verdes et al. [in press]


202 CHAPTER 6. FORSCHUNGSSTELLE “RADIOMETRIE”<br />

6.1.12 The authigenic 10 Be/ 9 Be ratio in deep sea sediments as a proxy for<br />

the Earth‘s magnetic field intensity<br />

Participating scientists Patrick Wenderoth, M. Christl, F. Bernsdorff, A. Mangini, P. Kubik<br />

(Zürich)<br />

Abstract We tested if the authigenic 10 Be/ 9 Be ratio in deep sea sediments could be used for the<br />

reconstruction of the relative Earth’s magnetic field.<br />

Reconstruction of the relative Earth’s magnetic field strength for the last 580 ka<br />

relative Earth magnetic field,<br />

determined with 10 Be Titan corrected / 9 Be(auth.)/g sed<br />

from 10 Be Titancorrected / 9 Be(auth.)/g sed<br />

Relative Paleointensity from Sint800<br />

2,5<br />

2,0<br />

1,5<br />

1,0<br />

0,5<br />

0,0<br />

1 2 3 4 5 6 7 8<br />

Relative Paleointensity<br />

1,4<br />

1,2<br />

1,0<br />

0,8<br />

0,6<br />

0,4<br />

9 10 11 12 13 14 15 16 0,2<br />

0 0 100 200 200 300 400 400 500 600<br />

600<br />

Age (ka)<br />

Figure 6.11: The Relative Earth’s magnetic field, determined with 10 BeT itan corrected/ 9 Be(auth.)/gsed<br />

(blue curve) compared with the relative intensity derived from paleomagnetic data (SINT 800), (black<br />

curve).<br />

Background The production rate of the radionuclide<br />

10 Be in the stratosphere, induced by<br />

interaction of cosmic rays with atmospheric O<br />

and N, depends on the intensity of the Earth’s<br />

magnetic field. The production rate of 10 Be increases<br />

when the Earth’s magnetic field strength<br />

decreases and vice versa. Therefore, the 10 Beflux<br />

in the deep sea sediments is a proxy for the<br />

longterm variation of the relative Earth’s magnetic<br />

field. However, the 10 Be-flux into sediments<br />

has to be normalized with 230 T h to account for<br />

processes that redistribute the sediments on the<br />

sea floor. This normalization is limited to the last<br />

350 ky. Here, a new method was investigated,<br />

based on the normalization to the stable isotope<br />

9 Be. The 10 Be/ 9 Be ratio depends only on the<br />

half life of 10 Be (1.5 Ma). Deep sea sediments<br />

have a detritic and an authigenic (i.e sea water signature)<br />

component. Both 10 Be and 9 Be detritic<br />

fluxes may be influenced by climate [McHargue et<br />

al., 2005], whereas the normalization of 10 Be on<br />

authigenic 9 Be is not.<br />

Funding Diplomathesis, non in this case.<br />

1,6<br />

Methods and results In this study a procedure<br />

based on sequential extraction steps was developed<br />

to separate the authigenic and the terrigenous<br />

components of sediments from ODP Leg<br />

177 Site 1089. In addition, Ti in the authigenic<br />

fraction was measured to quantify the amount of<br />

extracted detritic fraction.<br />

The 10 Be-flux normalized to the 10 Be/ 9 Be ratio<br />

was compared with that derived from the 230 T h<br />

normalization. Best matching was obtained when<br />

the 10 Be-flux was normalized to authigenic 9 Be<br />

and additionally using a ”Ti-correction”. The<br />

magnetic field reconstruction determined by the<br />

”Ti corrected” authigenic 10 Be/ 9 Be ratio correlates<br />

well with the record from paleomagnetic data<br />

(SINT 800) for the last 580ka (Fig. 6.11). Furthermore,<br />

we could show that the signal of paleomagnetic<br />

intensity of Site 1089 is partially an artifact<br />

of supply of terrigenuos material and, therefore,<br />

not as appropriate as the 10 Be-flux for reconstructing<br />

the Earth’s magnetic field<br />

Main publication Wenderoth [2005]


6.1. RADIOMETRIC DATING OF WATER AND SEDIMENTS 203<br />

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Bibliography<br />

Peer Reviewed Publications . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 209<br />

Grey Publications . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 215<br />

PhD Theses . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 217<br />

Diploma Theses . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 219<br />

Invited Talks . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 221<br />

207


7.1. PEER REVIEWED PUBLICATIONS 209<br />

Peer Reviewed Publications<br />

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Bobrowski, N., Hönninger, G., Lohberger, F., & Platt, U. 2005. IDOAS: A new monitoring technique<br />

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Braun, H. in press. Possible solar origin of the glacial 1,470-year climate cycle demonstrated in a<br />

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Braun, H., Christl, M., Rahmstorf, S., Ganopolski, A., Mangini, A., Kubatzki, C., Roth, K., &<br />

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skylight absorption measurements. Appl.Opt., 43(22), 4415 – 4426.<br />

Bulath, S., Alekhina, I., Blot, M., Petit, J.-R., de Angelis, M., Wagenbach, D., Lipenkov, V., Valilyeva,<br />

L., Wloch, D., Raynaud, D., & Lukin, V. 2004. DNA singature of thermophilic bacteria from the<br />

aged accretion ice of Lake Vostok, Antarctica: implications for searching for life in extreme icy<br />

environments. International Journal of Astrobiology, 3(1), 1–12.<br />

Butz, A., Bösch, H., Camy-Peyret, C., Chipperfield, M., Dorf, M., Dufour, G., Grunow, K., Jeseck,<br />

P., Kühl, S., Payan, S., Pepin, I., Pukite, J., Rozanov, A., von Savigny, C., Sioris, C., Wagner, T.,<br />

Weidner, F., & Pfeilsticker, K. 2005. Inter-comparison of Stratospheric O3 and NO2 abundances retrieved<br />

from balloon borne direct sun observations and Envisat/SCIAMACHY limb measurements.<br />

Atmos. Chem. Phys. Disc., 5, 10747 – 10797.<br />

Canty, T., Salawitch, R.S., Renard, J.B., Reviere, E.D., Pfeilsticker, K., M., Dorf., Fitzenberger,<br />

R., Bösch, H., Stimpfle, R.M., Wilmouth, D.M., Anderson, J.G., Richard, E.C., Fahey, D.W., &<br />

Gao, R.S.and Bui, T.P. 2005. Analysis of BrO, ClO, and nighttime OClO in the arctic winter<br />

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Christl, M., Mangini, A., Holzkämper, S., & Spötl, C. 2004. Evidence for a link between the flux<br />

of galactic cosmic rays and Earths climate during the past 200,000 years. J. Atmospheric and<br />

Solar-Terrestrial Physics, 66, 313–322.<br />

Corcho Alvarado, J. A., Purtschert, R., Hinsby, K., Troldborg, L., Hofer, M., Kipfer, R., Aeschbach-<br />

Hertig, W., & Synal, H.-A. 2004. 36 Cl in modern groundwater dated by a multi tracer approach<br />

( 3 H/ 3 He, SF6, CFC-12 and 85 Kr): A case study in quaternary sand aquifers in the Odense Pilot<br />

River Basin, Denmark. Appl. Geochem., 20, 599–609.<br />

Corsmeier, U., Kohler, M., Vogel, B., Vogel, H., & Fiedler, F. 2005. BAB II: a project to evaluate the<br />

accuracy of real-world traffic emissions for a motorway. Atmos. Environ., 39, 5627–5641.<br />

Crewell, S., Bloemink, H., Feijt, A., García, S.G., Jolivet, D., Krasnov, O.A., van Lammeren, A.,<br />

Löhnert, U., van Meijgaard, E., Meywerk, J., Quante, M., Pfeilsticker, K., Schmidt, S., Scholl, T.,<br />

Simmer, C., Schröder, M., Trautmann, T., Venema, V., Wendisch, M., & Willén, U. 2004. The<br />

BALTEX Bridge Campaign - An integrated approach for a better understanding of clouds. Bull.<br />

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Dufour, G., Payan, S., Lefévre, F., Berthet, G., Eremenko, M., Butz, A., Jeseck, P., Té, Y., Pfeilsticker,<br />

K., & Camy-Peyret, C. 2005. 4D comparison method to study the NOy partitioning in summer<br />

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210 CHAPTER 7. BIBLIOGRAPHY<br />

Eitel, B., Hecht, S., Mächtle, B., Schukraft, G., Kadereit, A., Wagner, G.A., Kromer, B., Unkel, I., &<br />

Reindel, M. 2005. Geoarchaeological evidence from desert loess in the Nazca/Palpa region, Southern<br />

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Fix, A., Ehret, G., Flentje, H., Poberaj, G., Gottwald, M., Finkenzeller, H., Bremer, H., Bruns, M.,<br />

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Frankenberg, C., Platt, U., & Wagner, T. 2005c. Retrieval of CO from SCIAMACHY onboard<br />

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Junkermann, W., Astorga-Llorens, C., Larsen, B. R., Mellqvist, J., Strandberg, A., Yu, Y., Galle,<br />

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Hendrick, F., Barret, B., Van Roozendael, M., Boesch, H., Butz, A., De Mazière, M., Goutail, F.,<br />

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Hollwedel, J., Wenig, M., Beirle, S., Kraus, S., Kühl, S., Wilms-Grabe, W., Platt, U., & Wagner, T.<br />

2004. Year-to-Year Variations of Spring Time Polar Tropospheric BrO as seen by GOME. Adv.<br />

Space Res., 34, 804–808. doi:10.1016/j.asr.2003.08.060.<br />

Holzkämper, S., Mangini, A., Spötl, C., & Mudelsee, M. 2004. Timing and progression of the Last<br />

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Holzkämper, S., Spötl, C., & Mangini, A. 2005. High-precision constrains on timing of Alpine warm<br />

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Hughen, K., Lehman, S., Southon, J., Overpeck, J., Marchal, O., & Herring, C. 2004a. 14C activity<br />

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Hughen, K.A., Baillie, M.G.L., Bard, E., Beck, J.W., Bertrand, C.J.H., J.H., Chanda, Blackwell, P.G.,<br />

Buck, C.E., Burr, G.S., Cutler, K.B., Damon, P.E., Edwards, R.L., Fairbanks, R.G., Richard, G.,<br />

Friedrich, M., Guilderson, T.P., Kromer, B., McCormac, G., Manning, S., Ramsey, C.B., Reimer,<br />

P.J., Reimer, R.W., Remmele, S., Southon, J.R., Stuiver, M, Talamo, S., Taylor, F.W., van der<br />

Plicht, J., & Weyhenmeyer, C.E. 2004b. Marine04 Marine Radiocarbon Age Calibration, 0-26 Cal<br />

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Jähne, B., Schmidt, M., & Rocholz, R. 2005c. Combined optical slope/height measurements of short<br />

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Kern, C., Trick, S., Rippel, B., & Platt, U. 2005. Applicability of light-emitting diodes as light sources<br />

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Khokhar, M.F., Frankenberg, C., Roozendael, M. Van, Beirle, S., Kühl, S., Richter, A., Platt, U.,<br />

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Kromer, B., Friedrich, M., Hughen, K.A., Kaiser, F., Remmele, S., Schaub, M., & Talamo, S. 2004.<br />

Late Glacial 14C ages from a floating 1382-ring pine chronology. Radiocarbon, 46(3), 1203–1209.<br />

Kühl, S., D”ornbrack, A., Sinnhuber, B.-M., Wilms-Grabe, W., Platt, U., & Wagner, T. 2004. Observational<br />

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Laepple, T., Knab, V., Mettendorf, K.-U., & Pundt, I. 2004. Longpath DOAS tomography on a<br />

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Jähne, B. 2004. Handbook of Digital Image Processing for Scientific and Technical Applications. 2nd<br />

edn. Boca Raton: CRC Press.<br />

Jähne, B. 2005a. Digital Image Processing. 6th edn. Berlin: Springer.<br />

Jähne, B. 2005b. Digitale Bildverarbeitung. 6th edn. Berlin: Springer.<br />

Kreuzer, A. M., Zongyu, C., Kipfer, R., & Aeschbach-Hertig, W. in press 2005. Environmental Tracers<br />

in Groundwater of the North China Plain. In: IAEA (ed), International Conference on Isotopes in<br />

Environmental Studies - Aquatic Forum 2004. Monte-Carlo, Monaco: IAEA.<br />

Marbach, T., Beirle, S., Hollwedel, J., Platt, U., & Wagner, T. 2004. Identification of tropospheric<br />

emission sources from satellite observations: Synergistic use of trace gas measurements of formaldehyde<br />

(HCHO), and nitrogen dioxide (NO2). In: Proceedings of the ENVISAT & ERS Symposium,<br />

6-10 September 2004, Salzburg, Austria. ESA publication SP-572, (CD-ROM).<br />

Pettinger, M., Keck, L., Fischer, H., Wagenbach, D., Preunkert, S., Böhm, R., Hoelzle, M., & Hoffmann,<br />

M. Leuenbergerand G. 2005. Cenntennial scale isotope thermometry from Alpine ice core<br />

records: shortcomings and challenge. Geophysical Research Abstracts, Vol 7, 07941.<br />

Platt, U., Pfeilsticker, K., & Vollmer, M. 2005. Chapter 24: Atmospheric Optics. In: Träger, F. (ed),<br />

Springer Handbook of Lasers and Optics. Heidelberg: Springer.


216 CHAPTER 7. BIBLIOGRAPHY<br />

Poehler, D., Rippel, B., Stelzer, A., Mettendorf, K. U., Hartl, A., Platt, U., & Pundt, I. 2005.<br />

Instrumental setup and measurement configuration for 2D-tomographic DOAS measurements of<br />

trace gas distributions over an area of a few square km. In: Proceedings of the 31st ”International<br />

Symposium of Remote Sensing of the Environment”, June 20-24, 2005, in St. Petersburg, Russia.<br />

ISPRS-publication(CD-ROM).<br />

Pundt, I., Hak, C., Hartl, A., Heue, K.-P., Mettendorf, K. U., Platt, U., Poehler, D., Rippel, B., Song,<br />

B.-C., Stelzer, A., Wagner, T., Bruns, M., Burrows, J. P., Richter, A., & Wang, P. 2005. Mapping of<br />

tropospheric trace gas concentration distributions from ground and aircraft by DOAS-tomography<br />

(Tom-DOAS). In: Proceedings of the 31st ”International Symposium of Remote Sensing of the<br />

Environment”, June 20-24, 2005, in St. Petersburg, Russia. ISPRS-publication(CD-ROM).<br />

Schock, M., Greilich, S., Wagenbach, D., Preunkert, S., Legrand, M., Petit, J. R., Flückiger, J.,<br />

Leuenberger, M., Haeberli, W., & Psenner, R. 2005. Dissolved organic carbon (DOC) in ice samples<br />

from non-temperated, polar and Alpine glaciers. Geophysical Research Abstracts, Vol. 7, 08671.<br />

Scholz, D., & Mangini, A. in press. U-redistribution in fossil reef corals from Barbados, West Indies,<br />

and sea level reconstruction for MIS 6.5. In: Sirocko, F., Litt, T., Claussen, M., & Sanchez Goni,<br />

M.-F. (eds), The climate of past interglacials.<br />

Schröder Ritzrau, A., Freiwald, A., & Mangini, A. 2005. U/Th dating of deep-water corals from the<br />

eastern North Atlantic and the western Mediterranean Sea. In: Freiwald, A., & Roberts, J.M.<br />

(eds), Cold-water corals and ecosystems. Berlin Heidelberg: Springer-Verlag.<br />

Spötl, C., Mangini, A., Burns, S.J., Frank, N., & Pavuza, R. 2004. Speleothems from high alpine<br />

Spannagel Cave, Zillertal Alps (Austria). Page 329 of: Sasowsky, I., & MyIroie, J. (eds), Studies of<br />

Cave Sediments. New York: Kluwer Academic.<br />

Steier, P., Drosg, R., Kutschera, W., Wild, E. M., Fedi, M., Wagenbach, D., & Schock, M. 2005.<br />

Radiocarbon determination of particulate organic carbon (POC) in non-temperated, Alpine glacier<br />

ice (Abstract). The 10th International Conference on Accelerator Mass Spectrometry Berkeley,<br />

California, September 5-10, 2005.<br />

Volkamer, R., Barnes, I., Platt, U., Molina, L. T., & Molina, M. J. 2004. Remote Sensing of Glyoxal<br />

by Differential Optical Absorption Spectrosocopy (DOAS): Advancements in Simulation Chamber<br />

and Field Experiments. In: Rudzinski, K., & Barnes, I. (eds), NATO Advanced Research Workshop<br />

of Environmental Simulation Chambers - Application to Atmospheric Chemical Processes, vol.<br />

NATO Sciences Series, IV. Earth and Environmental Sciences. Zakopane, Poland: Kluwer Academic<br />

Publishers.<br />

von Glasow, R. 2005. Lead Essay - Research Front Iodine. Env. Chem., 2, in press.<br />

von Rohden, C., Hauser, A., Wunderle, K., Ilmberger, J., Wittum, G., & Roth, K. 2005. Lake<br />

dynamics: observation and high-resolution numerical simulation. In Rannacher editor. Springer.<br />

Wegner, A., Rohlfs, J., Huke, M., Stanzick, A., Wagenbach, D., Oerter, H., Sommer, S., Mulvaney,<br />

R., & Kubik, P. 2005. Bi-annual to decadal 10 Be variability in firn cores from Dronning Maud Land<br />

(DML) and Berkner Island (BI), Antarctica. Geophysical Research Abstracts, Vol 7, 08396.<br />

Wilms-Grabe, W., Kühl, S., Beirle, S., Platt, U., & Wagner, T. 2004. GOME observations of stratospheric<br />

trace gas distributions during the split vortex event in the Antarctic winter 2002. Pages<br />

1053–1054 of: Proceedings Quadrennial Ozone Symposium, 1-8 June 2004, Kos, Greece.


7.3. PHD THESES 217<br />

PhD Theses<br />

Bayer, A. 2005. X-ray attenuation techniques to explore the dynamics of water in porous media. PhD<br />

thesis, University of Heidelberg.<br />

Beirle, S. 2004. Estimating source strengths and lifetime of Nitrogen Oxides from satellite data. Ph.D.<br />

thesis, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />

Bobrowski, N. 2005. Volcanic Gas Studies by MAX-DOAS. Dissertation, <strong>Universität</strong> Heidelberg.<br />

Dorf, M. 2005. Investigation of inorganic stratospheric bromine by balloon-borne DOAS measurements<br />

and model simulations. PhD thesis, University of Heidelberg, Heidelberg, Germany.<br />

El-Gamal, H. 2005. Environmental tracers in groundwater as tools to study hydrological questions in<br />

arid regions. PhD thesis, University of Heidelberg.<br />

Frankenberg, C. 2005. Retrieval of Methane and Carbon Monoxide using near infrared spectra recorded<br />

by SCIAMACHY onboard ENVISAT - Algorithm development and data analysis. Ph.D. thesis,<br />

<strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />

Fuß, D. 2004. Kombinierte Höhen- und Neigungsmessung von winderzeugten Wasserwellen am Heidelberger<br />

Aeolotron. PhD Thesis, <strong>Universität</strong> Heidelberg.<br />

Heue, K.-P. 2005a. Airborne Multi Axis DOAS instrument and measurements of two dimensional<br />

tropospheric trace gas distributions. Ph.D. thesis, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg,<br />

Germany.<br />

Heue, K.-P. 2005b. Airborne multi axis DOAS instrument and measurements of two dimensional<br />

tropospheric trace gas distributions. Ph.D. thesis, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg,<br />

Germany.<br />

Hilsenstein, V. 2004. Design and Implementation of a Passive Stereo-Infrared Imaging System for the<br />

Surface Reconstruction of Water Waves. Ph.D. thesis, <strong>Universität</strong> Heidelberg.<br />

Hollwedel, J. 2005. Observations of tropospheric and stratospheric Bromine Monoxide from satellite.<br />

Ph.D. thesis, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />

Klar, M. 2005. Design of an endoscopic 3-D Particle-Tracking Velocimetry system and its application<br />

in flow measurements within a gravel layer. Ph.D. thesis, <strong>Universität</strong> Heidelberg.<br />

Kühl, S. 2005. Quantifying stratospheric chlorine chemistry by the satellite spectrometers GOME and<br />

SCIAMACHY. Ph.D. thesis, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />

Mettendorf, K. U. 2005. Aufbau und Einsatz eines Multibeam Instrumentes zur DOAStomographischen<br />

Messung zweidimensionaler Konzentrationsverteilungen. Ph.D. thesis, <strong>Institut</strong><br />

<strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />

Naegler, T. 2005 (June). Simulating Bomb Radiocarbon: Consequences for the Global Carbon Cycle.<br />

Ph.D. thesis, Insititut <strong>für</strong> <strong>Umweltphysik</strong>, University of Heidelberg, Heidelberg, Germany.<br />

Nielsen, R. 2004. Hochgenaue Messung der Schmidtzahlabhängigkeit des Gasaustausches an einer<br />

wind- und wellenbewegten Wasseroberfläche. Ph.D. thesis, <strong>Universität</strong> Heidelberg.<br />

Peters, C. 2005. Studies of Reactive Halogen Species (RHS) in the Marine and mid-Latitudinal Boundary<br />

Layer by Active Longpath Differential Optical Absorption Spectroscopy. Dissertation, <strong>Universität</strong><br />

Heidelberg.<br />

Schimpf, D. 2005. Datierung und Interpretation der Kohlenstoff- und Sauerstoffisotopie zweier<br />

holozäner Stalagmiten aus dem Süden Chiles (Patagonien). unpublished Master Thesis, University<br />

of Heidelberg, <strong>Institut</strong>e of Environmental Physics.<br />

Scholz, D. 2005. U-series dating of diagenetically altered fossil reef corals and the application for sea<br />

level reconstruction. unpublished PhD Thesis, University of Heidelberg, Heidelberger Akademie der<br />

Wissenschaften.<br />

Schulze, B. 2005. Hochaufgelöste Rekonstruktion der 10Be-Produktionsrate aus Tiefseesedimentkernen<br />

des Bermuda Rise über die letzten 70.000 Jahre. unpublished Master Thesis, University of<br />

Heidelberg, <strong>Institut</strong>e of Environmental Physics.


218 CHAPTER 7. BIBLIOGRAPHY<br />

Weidner, F. 2005. Development and application of a versatile balloon-borne DOAS instrument for<br />

skylight radiance and atmospheric trace gas measurements. PhD thesis, University of Heidelberg,<br />

Heidelberg, Germany.<br />

Wenderoth, P. 2005. Untersuchung der Anwendbarkeit des authigenen 10 Be/ 9 Be-Verhältnisses in Tiefseesedimenten<br />

als Proxy zur Rekonstruktion der Erdmagnetfeldstärke. unpublished Master Thesis,<br />

University of Heidelberg, <strong>Institut</strong>e of Environmental Physics.


7.4. DIPLOMA THESES 219<br />

Diploma Theses<br />

Bäuerle, A. 2004. Messung von Spurenstoffverteilungen in Mailand mit Hilfe eines Multistrahl-<br />

Langpfad Teleskops. Staatsexamensarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />

Bengel, I. 2005. Spurenstoffglaziologische Pilotuntersuchungen an einer kalten Miniatureiskappe.<br />

Diplomarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg.<br />

Bobrowski, N., & Filsinger, F. 2005. Mini-MAX-DOAS Manual. <strong>Universität</strong> Heidelberg.<br />

Halasia, M.-A. 2004. SMAX-DOAS observation of atmospheric trace gases on the Polarstern<br />

ANT/XX-expedition from October 2002 until February 2003. Diplomarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>,<br />

<strong>Universität</strong> Heidelberg.<br />

Herzog, A. 2005. Free Parameterisation of Soil Hydraulic Properties. Diplomarbeit, University of<br />

Heidelberg.<br />

Kern, C. 2004. Applicability of light-emitting diodes as light sources for long path DOAS measurements:<br />

A feasibility study. Diplomarbeit, <strong>Universität</strong> Heidelberg.<br />

Klement, R. 2005. Optimierung von SF6-Grundwasserprobenahme-Methoden. Diplomarbeit, <strong>Universität</strong><br />

Heidelberg.<br />

Kluge, T. 2005. Radon als Tracer in aquatischen Systemen. Diplomarbeit, <strong>Universität</strong> Heidelberg.<br />

Knab, V. 2004. Basic theory on DOAS tomography, Reconstruction of 2D trace gas distributions by<br />

discrete linear inversion techniques. Diplomarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg,<br />

Germany.<br />

Lindner, A. 2005. Ballongestütze Messungen der extraterrestrischen spektralen solaren Irradianz.<br />

Diploma thesis, University of Heidelberg, Heidelberg, Germany.<br />

Louban, I. 2005. Zweidimensionale Aufnahmen von Spurenstoff-Verteilungen. Diplomarbeit, <strong>Universität</strong><br />

Heidelberg.<br />

May, B. 2005. Quantification of the fossile fraction of carbonaceous aerosol by radiocarbon analysis.<br />

Diplomarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg.<br />

Reichl, U. 2005. Ground-based direct Sun UV/vis spectroscopy in Timon/Northeastern Brazil: Comparison<br />

of tropospheric air mass pollution in the dry and wet season. Diploma thesis, University of<br />

Heidelberg, Heidelberg, Germany.<br />

Rice, S. 2004. The development of a method for the extraction and measurement of noble gases from<br />

fluid inclusions in samples of calcium carbonate. Master thesis, University of Heidelberg.<br />

Rippel, B. 2005. Vorarbeiten <strong>für</strong> Langpfad DOAS Tomographische Messungen über der Stadt Heidelberg.<br />

Diplomarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />

Rocholz, R. 2005. Bildgebendes System zur simultanen Neigungs- und Höhenmessung an kleinskaligen<br />

Wind-Wasser-Wellen. diploma thesis, <strong>Universität</strong> Heidelberg.<br />

Schell, S. 2004. 222 Radon-Profil-Messungen in Süd- und Ostdeutschland, Anwendung der Radon-<br />

Tracer-Methode zur Berechnung von CO2- und CH4-Flüssen. Diplomarbeit, Insititut <strong>für</strong> <strong>Umweltphysik</strong>,<br />

University of Heidelberg. in German.<br />

Schönherr, C. 2005 (October). Investigating Carbon Dioxide, Carbon Monoxide and Fossil Fuel CO2<br />

in Heidelberg. Diplomarbeit, Insititut <strong>für</strong> <strong>Umweltphysik</strong>, University of Heidelberg.<br />

Schwarz, T. 2005. Development of a depth resolving boundary layer visualization for gas exchange at<br />

free water surfaces. diploma thesis, <strong>Universität</strong> Heidelberg.<br />

Schwärzle, J. 2005. Spektroskopische Messung von Halogenoxiden in der marinen atmosphärischen<br />

Grenzschicht in Alcântara/Brasilien. Staatsexamensarbeit, University of Heidelberg, Heidelberg,<br />

Germany.<br />

Seitz, K. 2005. Spektroskopische Langzeitmessungen von Spurengasen in der freien Troposphäre.<br />

Diplomarbeit, <strong>Universität</strong> Heidelberg.


220 CHAPTER 7. BIBLIOGRAPHY<br />

Stelzer, A. 2005. Horizontale tomographische Langpfad-DOAS Spurengasmessungen in Heidelberg.<br />

Diplomarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />

Träumner, K. 2005. Inbetriebnahme, Tests und erste Anwendung einer neuen Aufbereitungslinie zur<br />

massenspektrometrischen Messung von Edelgasen aus Grundwasser - und Stalagmitproben. Diplomarbeit,<br />

<strong>Universität</strong> Heidelberg.<br />

Ulbrich, C. 2005. Monitoring Field Tracer Experiment with Ground Penetrating Radar and Time<br />

Domain Reflectometry. Diplomarbeit, University of Heidelberg.<br />

Wunderle, K. 2005. Untersuchungen der Strömungen im Willersinnweiher mit einem akustischen<br />

Strömungsmessgerät. Diplomarbeit, University of Heidelberg.


7.5. INVITED TALKS 221<br />

Invited Talks<br />

Aeschbach-Hertig, W. 2004a. Climate of the Past as a Basis for an Assessment of the Future. Invited<br />

talk, GSI-Kolloquium, Darmstadt, Germany.<br />

Aeschbach-Hertig, W. 2004b. Environmental Tracers in Groundwater Studies - Water Resources and<br />

Paleoclimate. Invited talk, <strong>Institut</strong>e of Hydrogeology and Environmental Geology, Chinese Academy<br />

of Geological Sciences, Zhengding, China.<br />

Aeschbach-Hertig, W. 2004c. Excess Air in Groundwater: Problems and Opportunities. Invited<br />

keynote presentation, Annual Meeting of the Geological Society of America (GSA), Denver, USA.<br />

Aeschbach-Hertig, W. 2004d. Noble Gases and Excess Air in Groundwater: Review and Outlook.<br />

Invited talk, KUP-Seminar, University of Bern, Switzerland.<br />

Aeschbach-Hertig, W. 2005. Surface and Subsurface Waters. Invited lecture, WE-Heraeus summerschool<br />

”Physics of the Environment”, Bad Honnef, Germany.<br />

Bobrowski, N. 2004. The DOAS (Differential Optical Absorption Spectroscopy) principle - experimental<br />

setups and mathematical description of the DOAS problem and Development of the Mini-MAX-<br />

DOAS (Multi-AXis Differntial Optical Absorption Spectroscopy) and examples of applications at<br />

three Italian volcanoes - Stromboli, Vulcano, Etna. Invited talk, Seminar INGV Palermo.<br />

Bobrowski, N. 2005a. DOAS evaluation basics. Invited talk, IAVCEI Gas workshop 9th, Nicolosi.<br />

Bobrowski, N. 2005b. The DOAS technique and the analyses of gas emissions of active volcanoes.<br />

Invited talk, Seminar ”Stoffbestand und Entwicklung von Mantel und Kruste”, Mainz.<br />

Bobrowski, N. 2005c. Volcanic research carried out with the DOAS technique - an overview. Invited<br />

talk, Seminar at CAI Pedara.<br />

Butz, A. 2005. LPMA/DOAS: Balloon based SCIAMACHY validation example: O3 and NO2 vertical<br />

profiles. Invited talk, SCIAMACHY Science Advisory Group 32, Delft, Netherlands.<br />

Jähne, B. 2004a. Exchange Processes at the Ocean Surface: Their Role in Coupling Atmosphere and<br />

Ocean, A Contribution to the SOLAS Project. Invited talk, Hauptvortrag Fachverband <strong>Umweltphysik</strong>,<br />

DPG Frühjahrstagung München, 22. Mrz 2004.<br />

Jähne, B. 2004b. New Insight into the Mechanisms of Air-Sea Gas Transfer. Invited talk, IOW-<br />

Kolloquium, Leibniz-<strong>Institut</strong> fr Ostseeforschung, Warnemünde, Januar 2004.<br />

Jähne, B., & Garbe, C. S. 2004. Spatiotemporal Active Thermography. Invited talk, 7th International<br />

Conference on Quantitative Infrared Thermography, von Karman <strong>Institut</strong>e for Fluid Dynamics in<br />

Rhode Saint Genèse, Belgium, 08. July 2004.<br />

Jähne, B., Nielsen, R., Popp, C., Schimpf, U., & Garbe, C. S. 2005. Air-Sea Gas Transfer: Schmidt<br />

Number Dependency and Intermittency. Invited talk, 37th International Liège Colloquium on Ocean<br />

Dynamics Gas Transfer at Water Surfaces, 2–6 May 2005.<br />

Levin, I. 2004a. Greenhouse Gases Trends in Europe and at the German Antarctic Station. Invited<br />

talk, WMO WMO/GAW Expert Workshop on The Quality and Applications of European GAW<br />

Measurements. Tutzing, Germany.<br />

Levin, I. 2004b. Quantification of Exchange Rates in the Global Carbon Cycle by Radiocarbon Observations.<br />

Invited talk, Physical Colloquium. University of Groningen, The Netherlands.<br />

Levin, I. 2005a. Quantifying fossil fuel CO2 over Europe. Invited talk, Workshop on A Blueprint for<br />

a GHG monitoring system in Europe. Amsterdam, The Netherlands.<br />

Levin, I. 2005b. Recent Heidelberg Radiocarbon Observations in Atmospheric CO2. Invited talk,<br />

13th International WMO Experts Meeting on atmospheric CO2 and Related Tracer Measurement<br />

Techniques. Boulder (CO) USA.<br />

Oswald, Benedikt, & Roth, Kurt. 2005. Parallel 3D Finite Element Time Domain Maxwell Solver<br />

- Investigation of Ground Penetrating Radar Sub-Wavelength Resolution. Paul Scherrer <strong>Institut</strong>,<br />

Villigen. 2005, August, 25.


222 CHAPTER 7. BIBLIOGRAPHY<br />

Pechtl, S. 2005. Halogenchemie in der Troposphäre: Überblick und Beispiele <strong>für</strong> Prozessstudien mit<br />

numerischen Modellen. Invited talk, the DLR, Oberpfaffenhofen, 15.11.2005.<br />

Pfeilsticker, K. 2005a. Collisional complexes, metastable, and stable complexes in the atmosphere,<br />

and their potential importance for the absorption of solar radiation. Invited talk, Gordon Research<br />

Conference on Radiation & Climate, Colby College, Waterville, ME, USA, July 24-29.<br />

Pfeilsticker, K. 2005b. Recent cloudy sky photon path <strong>pdf</strong> measurements from Heidelberg. Invited talk,<br />

3rd I3RC Workshop, IFM Kiel, October 11-14.<br />

Pfeilsticker, K., Lotter, A., Boesch, H., & Peters, C. 2004. Collisional complexes, metastable and stable<br />

dimers in the atmosphere, and their potential importance for the absorption of solar radiation. 228th<br />

National ACS Meeting, Philadelphia, PA, USA, August 22-26.<br />

Piot, M., & von Glasow, R. 2005. Sensitivity studies of ODEs and frost flowers with a numerical<br />

model. Invited talk, the OASIS workshop, Toronto, Canada, 20.09.2005.<br />

Platt, U. 2004a. Atmospheric Chemistry and Global Change. Invited talk, Reading, United Kingdom.<br />

Platt, U. 2004b. German SCIAMACHY Validation. Invited talk, SCIAMACHY Validation project<br />

final workshop, Bremen.<br />

Platt, U. 2004c. Reactive Halogen Species in the Troposphere. Invited talk, AFO-2000 Abschluß<br />

Workshop, Bad Tölz, 22.-2. März.<br />

Platt, U. 2004d. Spectroscopic Mapping of Trace Gases by Differential Optical Absorption Spectroscopy<br />

(DOAS). Invited talk, Massachusetts <strong>Institut</strong>e of Technology, Boston, Mass, USA.<br />

Platt, U. 2005a. Atmospheric Chemistry and Global Change. Invited talk, Advanced Environmental<br />

Monitoring Research Center, K-JIST, Kwangju, S. Korea.<br />

Platt, U. 2005b. Atmospheric Gas Phase Reactions. Invited talk, SOLAS Summer School, Cargese,<br />

Corsica, France.<br />

Platt, U. 2005c. The Determination of Reactive Halogen Species in the Troposphere and their Relevance<br />

for Atmospheric Chemistry. Invited talk, Workshop des DFG-Graduiertenkollegs 826,<br />

Elementspeziation: Methodenentwicklung und ihre Anwendung in den Umwelt- und Lebenswissenschaften,<br />

Mainz.<br />

Platt, U. 2005d. Neue Entwicklungen der atmosphärischen Spektroskopie - wie BERLIOZ II aussehen<br />

könnte. Invited talk, Seminar, Bergische <strong>Universität</strong> Wuppertal.<br />

Platt, U. 2005e. Observation of Spatial Distributions of Air Pollutants. Plenary lecture, Royal Meteorological<br />

Society Conference 2005, 12th-16th Sept. 2005, at the University of Exeter.<br />

Platt, U. 2005f. Ocean - Atmosphere Exchanges and Interactions. Invited talk, IGAC/WMO WORK-<br />

SHOP: From Chemical Weather Forecast to Climate Change in South America: the challenges and<br />

opportunities of integration and collaboration, Centro de Modelamiento Matemático, Universidad<br />

de Chile, Santiago de Chile.<br />

Platt, U. 2005g. Probing the Atmosphere with Differential Optical Absorption Spectroscopy - DOAS.<br />

Invited talk, Advanced Environmental Monitoring Research Center, K-JIST, Kwangju, S. Korea.<br />

Platt, U., & Burrows, J. P. 2005. The Remote Sensing of Atmospheric Constituents From Space,<br />

ACCENT-TROPOSAT-2 (AT2): An ACCENT Integration Task. Invited talk, ACCENT General<br />

Assembly, Clermont Ferrant, 9-11 Februar.<br />

Platt, U., & Zingler, J. 2006. Spatial Distribution of Halogen Oxides in the Dead Sea Basin, Israel<br />

Society for Ecology and Environmental Quality Sciences. Invited talk, Conference on ”Living with<br />

Global Change: Challenges in Environmental Sciences”, May 30 - June 1, 2005, Weizmann <strong>Institut</strong>e<br />

of Science, Israel.<br />

Platt, U., Sinreich, R., Friesß, U., & Wagner, T. 2005. Multi Axis Differential Optical Absorption Spectroscopy<br />

(MAX-DOAS) of Gas and Aerosol Distributions. Invited talk, 130th Faraday Discussion<br />

Meeting ”Atmospheric Chemistry”, Leeds, United Kingdom.


7.5. INVITED TALKS 223<br />

Pundt, I. 2005. DOAS (Differentielle Optische Absorptions- Spektroskopie) Messungen mit neuester<br />

Technologie. Invited talk, DECHEMA/GDCH/DGB-Gemeinschaftsausschuss Chemie der Atmosphre,<br />

Frankfurt, 22.04.2005.<br />

Pundt, I., Mettendorf, K.U., & v. Friedeburg, C. 2005. Emissionsmessung von NO2, SO2 und O3<br />

mittels DOAS Fernerkundung. Invited talk, workshop ”Validierung von Kfz-Emissionsdaten: Das<br />

<strong>Karls</strong>ruher Autobahnprojekt BAB II”, <strong>Karls</strong>ruhe, 01.12.2005.<br />

Roth, K. 2005a. Bodenwasser: Bedeutung – Herausforderung – Messung. Eröffnungsvortrag, Soil<br />

Moisture Group, <strong>Universität</strong> <strong>Karls</strong>ruhe, 8. Juni.<br />

Roth, K. 2005b. GPR zur Quantifizierung von Transportprozessen in Böden? <strong>Institut</strong> <strong>für</strong> Geophysik,<br />

<strong>Universität</strong> Kiel, 20. Mai.<br />

Roth, K. 2005c. Measurement and Modeling of Thermal and Hydraulic Dynamics of Permafrost Soils.<br />

Dept. of Earth Sciences, Uppsala University, March 31.<br />

Roth, K., & Wollschläger, U. 2005. Field-Scale Measurement of Soil Water Content. Plenary Session<br />

at International Conference on Human Impacts on Soil Quality Attributes, Isfahan, Iran, September<br />

12–16.<br />

Vogel, H.-J. 2005a. From Pore- to Continuum-Scale Understanding of Flow and Transport Processes<br />

in Porous Media. Keynote paper, SSSA-Annual Meeting, November 7-11, 2005, Salt Lake City,<br />

USA.<br />

Vogel, H.-J. 2005b. Hierarchies of flow and transport in soil. Keynote paper, GFHN, 29emes journees,<br />

November 24-25, 2004, Grenoble, France.<br />

Vogel, H.-J. 2005c. Modeling the heterogeneous structure of soil to predict flow and transport. SIAM<br />

Conference on Mathematical and Computational Issues in the Geosciences, June 7-10, 2005, Avignon,<br />

France.<br />

Vogel, H.-J., Samouelian, A., & Ippisch, O. 2005. Modeling structure to predict flow and transport.<br />

Gesellschaft <strong>für</strong> Angewandte Mathematik und Mechanik, 76th Annual Scientific Conference, March<br />

28 - April 1, 2005, Luxembourg.<br />

von Glasow, R. 2004a. Halogenchemie in der Troposphäre - Untersuchungen mit numerischen Modellen.<br />

Invited talk, the Insitut <strong>für</strong> Meteorologie und Klimaforschung, <strong>Karls</strong>ruhe, 02.11.2004.<br />

von Glasow, R. 2004b. Links between sulfur and halogen chemistry and implications for our climate.<br />

Invited talk, the Afred-Wegener-<strong>Institut</strong> <strong>für</strong> Meeresforschung, Bremerhaven, 05.02.2004.<br />

von Glasow, R. 2004c. Modeling of halogen chemistry: Overview and impact on sulfur cycle. Invited<br />

talk, the EGU meeting, Nice, 2004.<br />

von Glasow, R. 2004d. Sea salt aerosol chemistry: Brief overview and recent modeling results. Invited<br />

talk, the AAAR meeting, Atlanta, 2004.<br />

von Glasow, R. 2004e. Tropospheric halogen chemistry and its implications for O3 and sulfur in<br />

the boundary layer and free troposphere. Invited talk, the <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, Bremen,<br />

06.02.2004.<br />

von Glasow, R. 2005a. Invited talk, the AGU meeting, San Francisco, 2005.<br />

von Glasow, R. 2005b. Halogenchemie in der Troposphäre - Untersuchungen der Wechselwirkungen<br />

mit Ozon und Schwefel in Prozess- und globalen Modellstudien. Invited talk, the <strong>Institut</strong> <strong>für</strong><br />

Troposphärenforschung, Leipzig, 12.05.2005.<br />

von Glasow, R. 2005c. Impact of bromine on tropospheric photochemistry. Invited talk, the<br />

IGAC/SPARC workshop, Mainz, 19.05.2005.<br />

von Glasow, R. 2005d. Importance of the surface reaction OH + Cl- on sea salt aerosol for the<br />

chemistry of the MBL - a model study. Invited talk, the EMSI Workshop on Ions and Molecules at<br />

Aqueous Interfaces, Prague, Czech Republic, 27.06.2005.<br />

von Glasow, R. 2005e. Reactive halogen chemistry in the troposphere - Using numerical models for<br />

detailed process studies of the marine boundary layer and a first global assessment. Invited talk,<br />

NIWA, Lauder, New Zealand, 15.09.2005.


224 CHAPTER 7. BIBLIOGRAPHY<br />

von Glasow, R. 2005f. Reactive halogen chemistry in the troposphere - Using numerical models for<br />

detailed process studies of the marine boundary layer and a first global assessment. Invited talk,<br />

Harvard Univ., Cambridge, MA, USA, 08.04.2005.<br />

von Glasow, R. 2005g. Reactive halogen chemistry in the troposphere - Using numerical models for<br />

detailed process studies of the marine boundary layer and a first global assessment. Invited talk, the<br />

Univ. New Hampshire, Durham, USA, 07.04.2005.<br />

von Glasow, R. 2005h. Reactive halogen chemistry in the troposphere - Using numerical models for<br />

detailed process studies of the marine boundary layer and a first global assessment. Invited talk, the<br />

Univ. of East Anglia, Norwich, UK, 28.02.05.<br />

Wagenbach, D. 2004. Potential and restrictions of Alpine (mid-latitude) ice cores. Invited talk, SCIEM<br />

2000 (The synchronisation of civilization in the eastern Mediterranean in the 2nd Millenium BC)<br />

Workshop: Ashes and Ice, Vienna.<br />

Wagner, T. 2004a. Current status and future perspectives of atmospheric trace gas observations from<br />

space. Invited talk, <strong>Institut</strong>e Colloquium, MPI Mainz, Germany.<br />

Wagner, T. 2004b. Global monitoring of atmospheric trace gases, clouds and aerosols from<br />

UV/vis/NIR satellite instruments: Currents status and near future perspectives. Invited talk, SO-<br />

LAS Science conference, Halifax, Canada.<br />

Wagner, T. 2004c. Global monitoring of atmospheric trace gases, clouds and aerosols from<br />

UV/vis/NIR satellite instruments: Currents status and near future perspectives. Invited talk,<br />

WMO/GAW Expert Workshop, Tutzing, Germany.<br />

Wagner, T. 2004d. Moderne Methoden der Satellitenbildverarbeitung: Spektroskopie, Reflektions-,<br />

Streu-, und Absorptionsprozesse. Invited talk, WMO/GAW Expert Workshop, Tutzing, Germany.<br />

Wagner, T. 2005a. 7.5-year global trends in GOME cloud cover and humidity - a signal of climate<br />

change? Invited talk, KNMI, Utrecht, The Netherlands.<br />

Wagner, T. 2005b. Troposphärische Spurengasmessungen vom Satelliten aus. Invited talk,<br />

DECHEMA, Frankfurt, Germany.<br />

Wagner, T. 2005c. Wasserdampf-Fernerkundung mit dem ERS-2/GOME Sensor und seinen Nachfolgern.<br />

Invited talk, DWD, Offenbach, Germany.<br />

Zingler, J. 2005. Eine kurze Geschichte von Messungen zur Halogenchemie am Toten Meer, Israel.<br />

Invited talk, Seminar über aktuelle Forschungsthemen der Meteorologie, <strong>Institut</strong> <strong>für</strong> Meteorologie<br />

und Klimaforschung, Forschungszentrum <strong>Karls</strong>ruhe, <strong>Karls</strong>ruhe, Germany.


<strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong><br />

Im Neuenheimer Feld 229<br />

69120 Heidelberg<br />

Germany<br />

Tel. + 49 6221 54-63 50<br />

Fax + 49 6221 54-64 05<br />

email: sekretariat@iup.uni-heidelberg.de<br />

www.iup.uni-heidelberg.de<br />

Board of Directors<br />

Prof. Dr. Ulrich Platt<br />

Prof. Dr. Kurt Roth

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