-
Topics
Subnavigation
Topics
Electromagnetic fields
- What are electromagnetic fields?
- High-frequency fields
- Radiation protection in mobile communication
- Static and low-frequency fields
- Radiation protection relating to the expansion of the national grid
- Radiation protection in electromobility
- The Competence Centre for Electromagnetic Fields
Optical radiation
- What is optical radiation?
- UV radiation
- Visible light
- Infrared radiation
- Application in medicine and wellness
- Application in daily life and technology
Ionising radiation
- What is ionising radiation?
- Radioactivity in the environment
- Applications in medicine
- Applications in daily life and in technology
- Radioactive radiation sources in Germany
- Register high-level radioactive radiation sources
- Type approval procedure
- Items claiming to provide beneficial effects of radiation
- Cabin luggage security checks
- Radioactive materials in watches
- Ionisation smoke detectors (ISM)
- Radiation effects
- What are the effects of radiation?
- Effects of selected radioactive materials
- Consequences of a radiation accident
- Cancer and leukaemia
- Hereditary radiation damage
- Individual radiosensitivity
- Epidemiology of radiation-induced diseases
- Ionising radiation: positive effects?
- Radiation protection
- Nuclear accident management
- Service offers
-
The BfS
Subnavigation
The BfS
- Working at the BfS
- About us
- Science and research
- Laws and regulations
- Radiation Protection Act
- Ordinance on Protection against the Harmful Effects of Ionising Radiation
- Ordinance on Protection against the Harmful Effects of Non-ionising Radiation in Human Applications (NiSV)
- Frequently applied legal provisions
- Dose coefficients to calculate radiation exposure
- Links
Trace analysis at the BfS
- Using ultra-sensitive physical measurement systems the BfS is able to detect minute traces of airborne radioactive substances.
- Using these measurements, a clear distinction is possible between radioactive traces of natural or artificial origin.
- These measurements are referred to as trace analyses and are for example used for the verification of the worldwide ban on nuclear weapons tests.
Aims and objectives of trace analysis performed at the BfS are to
- detect minute quantities of natural and artificial airborne radioactivity as well as
- investigate its origin, distribution and dispersion in the environment and
- monitor short and long-term changes at the lowest activity-levels.
Legal foundations
Legal foundations for investigations within the scope of trace analysis are
- the Radiation Protection Law (Strahlenschutzgesetz) including measurement programmes given in the General Administrative Regulation on the Integrated Measurement and Information System for the monitoring of environmental radioactivity (AVV-IMIS),
- the European Atomic Energy Community (EURATOM) Treaty and
- the Comprehensive Nuclear-Test-Ban Treaty (CTBT).
The measurement results are summarized by the Coordinating Office for Trace Analysis at the BfS and are reported to the Federal Environment Ministry (BMUV), to the International Atomic Energy Agency (IAEA) as well as to the European Union (EU).
Monitoring results are also made available through an electronic system for emergency preparedness (ELAN) to report on the situation in the event of an incident (for example in case of an accident at a nuclear power plant).
Trace analysis air-borne particle collector on the roof of the BfS office in Freiburg
Air samples
At the monitoring station Schauinsland and in Freiburg samples of airborne dust and noble gases are collected and then prepared and analysed in the trace analysis laboratories in Freiburg.
The air dust and noble gas samples are collected continuously - generally for a week. If necessary (e.g. after the accident in Fukushima), precipitation samples are also taken and examined for radionuclides. In addition, noble gas samples from all over the world are analysed in the noble gas laboratory in Freiburg.
Laboratories
The BfS uses various laboratories for trace analysis:
Noble gas laboratory
Noble Gas Laboratory for trace analysis
- Accredited laboratory according to DIN EN ISO/IEC 17025:2018
Objectives
- environmental monitoring according to statutory obligations
- detecting clandestine nuclear activities
The radioactive isotopes of the noble gases xenon (for example xenon-133) and krypton (krypton-85) play an important role
- in detecting clandestine nuclear activities such as underground nuclear weapons testing and
- as an indicator of reprocessing of nuclear fuels, which is part of the production process of plutonium for nuclear weapons.
The BfS laboratory supports the Comprehensive Nuclear-Test-Ban Treaty Organisation (CTBTO) as a "support laboratory".
The BfS takes weekly air samples
- in Freiburg and
- on Mt. Schauinsland.
At currently six additional sampling stations around the world, weekly samples are collected in cooperation with institutions and analysed at the BfS noble gas laboratory. For this purpose, the samples are processed on-site and sent to the noble gas laboratory in pressurized cans or gas containers.
Method
A noble gas sample is prepared for the activity measurement.
In the noble gas laboratory, the air sample is processed using gas chromatography; this means that the gas mixture is separated into its individual chemical components.
The activity of the krypton fraction is then determined by measuring its beta radiation using proportional counters.
Finally, the gas volume of the analysed krypton fraction is determined chromatographically.
For the determination of the activities of the xenon isotopes the noble gas laboratory operates two nuclide-specific xenon measurement systems. These systems can measure activities and activity concentrations of the four xenon-isotopes
- xenon-133,
- xenon-135,
- xenon-131m and
- xenon-133m
by simultaneous measurement of beta- and gamma radiation. If xenon is detected in air samples, the measured isotopic composition can shed light on the potential sources of the xenon. This procedure has been accredited since March 2022.
In case of higher sample throughput there is the additional possibility to determine the xe-133 activities via the beta activity in analogy to the determination of the kr-85 activity.
Limits of detection
Typical activity detection limits of the proportional counter measurement systems are about 0.03 becquerel for krypton-85 and about 0.01 becquerel for xenon-133. For the nuclide specific system the activity detection limit is ca. 0.002 becquerel.
Gamma-spectrometry laboratory
Gamma-spectrometry laboratory for trace analysis
- Accredited laboratory according to DIN EN ISO/IEC 17025:2018
Objectives
- environmental monitoring according to statutory obligations
- Detection of traces of radioactivity in airborne dust samples
Traces of radioactive substances in airborne dust are detected using gamma-spectrometry. The required samples are taken using high-volume air samplers, the sampling duration is usually one week. In case of an incident with enhanced emissions of radionuclides to the air daily samples can be taken.
The measurements are aimed at determining activities and activity concentrations of various gamma-emitting radionuclides collected from the air using high volume samplers.
In order to detect traces of radioactivity, dust samples are analysed in the gamma-spectrometry laboratory of the Freiburg offices. These samples are taken
- at the monitoring station on Mount Schauinsland and
- on the roof of the Freiburg offices.
High volume samplers draw air through large-surface aerosol filters at an airflow of 700 to 900 cubic meters per hour. The dust particles with the adhering radionuclides deposit on these filters.
Method
Exposed aerosol filter after sampling
The filters are pressed into pellets at the end of each sampling period (usually one week). In order to detect traces of radionuclides, the pellets are measured for several days using highly sensitive high-purity germanium detectors. Lead shielding is used to reduce the influence from background radiation, which is present naturally everywhere and can interfere with the measurement.
Typical limits of detection for the activity concentration of caesium-137 are at around 0.1 microbecquerel per cubic metre of air.
Not all radionuclides can be identified by their gamma-ray emissions. Radionuclides such as strontium-90 or plutonium have to be radiochemically separated and processed before measurement. This is routinely performed on monthly samples in the radiochemistry laboratory of the Freiburg office.
Filters pressed into pellet shape
Monitoring for traces of radioactivity in airborne dust is part of the measurement programmes given in the General Administrative Regulation on the Integrated Measurement and Information System for the monitoring of environmental radioactivity (AVV-IMIS) and of the EURATOM treaty.
Measurements beyond the scope of accreditation
Gaseous iodine
Gaseous iodine in the air is not collected on the filters. In order to detect gaseous iodine, it is adsorbed on the surface of a solid (activated carbon for example). The sample produced in this process is analysed using gamma-spectrometry.
Precipitation samples
If required (after the Fukushima accident for example), precipitation samples are also taken at the monitoring station on Mount Schauinsland and at the Freiburg office, and are analysed for radionuclides. These samples contain radionuclides that have been washed out from the air by precipitation.
Radiochemistry laboratory
Radioanalytical laboratory
Objectives:
- environmental monitoring according to statutory obligations
Detecting radioactive elements in airborne dust samples:
- strontium
- uranium
- plutonium
- Detecting clandestine nuclear activities
Airborne dust samples collected at the monitoring station Schauinsland and in Freiburg are initially analysed in the gamma spectrometry laboratory. Then, in the radioanalytical laboratory, they are processed using radioanalytical methods to separate strontium, uranium and plutonium.
Method
In order to achieve the lowest possible limit of detection, between four and five weekly samples are combined to a monthly sample and subsequently ashed. The activity concentrations of strontium, uranium and plutonium are determined from the ashes of these samples.
The sample ash is dissolved in acid and processed in a specially designed microwave oven. Then, the nuclides to be determined are separated using radioanalytical methods and are deposited on filters or stainless steel planchets.
The strontium isotopes are measured using a low-level alpha/beta counter. This system is used for detecting the lowest detectable activities of alpha and beta emitters.
After electrochemical deposition on stainless steel planchets, the uranium and plutonium isotopes are measured in an alpha spectrometer.
Filter samples are processed in the radiochemistry laboratory
Limits of detection
With the described method, the following detection limits are achieved:
State of 2024.07.24