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New European demands as a challenge to develop new
technologies for the removal of micropollutants in
Environmental Technology University of Dortmund Emil-Figge-Str. 70 D-44221 Dortmund Phone: +49 231 755 2322 Fax:
With the European Water Framework Directive (EU-WRRL) , which came
into force on the 22nd Dec. 2000, the transfrontier water policy in Europe began.
The federal water act in Germany (WHG) was changed accordingly on the 25th
June 2002. With this the water resources policy started and the way for European
river basin management was levelled out. The essential aim of the guidelines is to
obtain an effective ecological water management with high standards. This means
for surface waters to reach a good chemical and a good ecological condition
within 15 years after the guideline was brought into force.
Attachment X of the EU-WRRL contains a list with prioritized and prioritized
dangerous water pollutants. Based on common European right binding agreements
should be worked out to restrict the entry of water pollutants and detectable
Prioritized Pollutants are persistent, toxic and have bio-accumulative
characteristics. For these pollutants the discharge, the emissions and the losses
into surface water are to be decreased step by step. There is also a quest that a
common agreement is found for quality specifications and emission restrictions.
In contrast the prioritized dangerous pollutants bare additional long-term risks due
to irreversible accumulation of biological-active organic-synthetic substances in
organisms and environmental systems. The intention is to end or gradually reduce
the discharges, emissions and losses within the next 20 years after approbation of
the European parliament and council .
Next to the already named pollutant in the attachment X of the EU-WRRL there
are other water relevant substances. Because of the amount that is released into
the aquatic environment and the finally not determined capability of polluting
surface waters the current discussions are still carrying on.
The main emitters of water pollutants (see Fig 1) are the municipal wastewater
treatment plants and the stormwater flow as well as the diffuse resources and
WWTP outflow 2
Ifosfamid Iop Iomepr
Generally there are different methods to remove water pollutants such as organic
and inorganic particles including soluble matter. The different techniques are
based on mechanical, chemical, biological and physical methods. In detail the
sedimentation, filtration, precipitation and flocculation are mentioned as well as
membrane-filtration (mikro-, nano- and ultra-filtration, reverse-osmoses),
adsorption with activated carbon and chemical-oxidative processes (see Fig 2).
For environmental compliance these methods can also be combined.
Whereas most of these methods only separate the harmful substances from the
water, the oxidative process causes degradation of the micro-pollutants. These are
removed out of the water by conversion, so that no other treatment is needed.
The modern municipal wastewater treatment plants are designed to eliminate
carbon, nitrogen and phosphate by means of biological and chemical treatment.
The customary process engineering is an aeration system that is in some cases
connected with a supplementing filtration plant.
Fig 2 – further technologies for the removal of water-impurities 
In one of the research projects, which have been promoted by the office of
environment and nature conservancy, agriculture and consumerism (German
abbr.: MUNLV), a definite elimination of pollutants was noticeable in the
different processing steps on a wastewater treatment plant. On the other hand
other pollutants pass through the plant without being eliminated in an appreciable
The total productivities of two big wastewater treatment plants have been
balanced as well as the elimination paths of the different treatments have been
investigated. In an accompanied experimental research on a semi-technical plant
the influence of various operating parameters was determined. The focus of the
examination was the sludge age, the concentration of the solid matter, the usage of
coagulant to eliminate phosphate and the applied bio-membrane reactors.
Only by varying the operating parameters, a satisfying degradation for the most of
the trace-elements could not be guarantied. Therefore it seems that the wastewater
treatment plant needs to be upgraded with a still to be determined tail-end-
technology for the proceeding wastewater treatment. This middle-term
economical solution is preferable to a deeper restructuring of the already existing
configuration of the plants. Possible alternative for the advanced wastewater
treatment can either be oxidation or adsorptive procedures.
This study was part of the NRW-Project “Untersuchungen zum Eintrag und zur
Elimination von gefährlichen Stoffen in kommunalen Kläranlagen”, which was
financially supported by the ministry for the environment and nature conservation,
agriculture and consumer protection of Nordrhein-Westfalen, Germany.
 Richtlinie 2000/60/EG des Europäischen Parlaments und des Rates zur
Schaffung eines Ordnungsrahmens für Maßnahmen der Gemeinschaft im Bereich der Abwasserpolitik, 2000
Untersuchungen zur oxidativen Eliminierung organischer
, Dissertation, Fraunhofer Institut für Umwelt-,
Sicherheits- und Energietechnik UMSICHT, Oberhausen, 1998
Helicobacter pylori gehört zu den Krankheitserregern, der beim Menschen am häufigsten zu Infektionen führt. Die Helicobacter pylori-Infektion wird überwiegend im Kleinkindesalter erworben und besteht in der Regel lebenslang fort, wenn nicht eine gezielte Therapie durchgeführt wird. Die Infektion ist für 80 - 90 % aller chroni-schen Entzündungen der Magenschleim- Eine Helicobacter
Biological activity of plant derived extracts against cancer tissue cultures Tova Cohen, Marina Tevrovski, Michal Maoz Biotechnology Engineering, ORT Braude College, P.O. Box 78, Karmiel 21982, Israel, Tel: 972-4-9901901, Fax: 972-4-9901738, E-mail: [email protected], [email protected] Keywords: Tissue cultures, plant extracts, synergism The general public is interested