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@PHDTHESIS{Sauter:994980,
      author       = {Sauter, Daniel},
      othercontributors = {Wintgens, Thomas Josef and Jekel, Martin},
      title        = {{T}he role of biological post-treatment following ozonation
                      in advanced municipal wastewater treatment},
      school       = {Rheinisch-Westfälische Technische Hochschule Aachen},
      type         = {Dissertation},
      address      = {Aachen},
      publisher    = {RWTH Aachen University},
      reportid     = {RWTH-2024-09636},
      pages        = {1 Online-Ressource : Illustrationen},
      year         = {2024},
      note         = {Veröffentlicht auf dem Publikationsserver der RWTH Aachen
                      University; Dissertation, Rheinisch-Westfälische Technische
                      Hochschule Aachen, 2024},
      abstract     = {Numerous municipal wastewater treatment plants (WWTP) in
                      Europe have been, are, and will be upgraded with ozonation
                      for organic micropollutant abatement. It is consensus that
                      ozonation requires a biological post-treatment step to abate
                      potentially toxic oxidation products formed by the reaction
                      of ozone. Several different post-treatment processes have
                      already been applied and investigated at full-scale,
                      however, specific target parameters and design guidelines
                      are still missing. This long-term pilot study provides a
                      comprehensive treatment performance assessment of different
                      biological post-treatment options and, based on that
                      information, derives general recommendations for the
                      post-treatment design. The investigated deep-bed filters and
                      constructed wetlands (CW) efficiently removed the oxidation
                      by-products (OBP) N-nitrosodimethylamine (NDMA) and carbonyl
                      compounds. The latter were degraded more slowly than NDMA,
                      resulting in a decrease of removal efficiency at low empty
                      bed contact times (EBCT) of 5 min in the deep-bed filters.
                      The long EBCT in the CW are not limiting for the removal of
                      the investigated OBP. A dual-media filter with sand and
                      biological activated carbon (S/BAC) outperformed a
                      non-adsorptive sand / anthracite filter (S/A) regarding the
                      removal of bulk organics. Also, the S/BAC filter abated a
                      number of OMP even at high treated bed volumes of >50,000,
                      which was not observed in the S/A filter. Enhanced
                      phosphorus removal could be implemented in the deep-bed
                      filters with low efforts by inline coagulant dosing into the
                      influent and did not impair the function as biological
                      post-treatment. Based on inactivation experiments with
                      sodium azide, the OMP removal in BAC filtration could only
                      be attributed to biotransformation for valsartan. Analysis
                      of the filter media-attached biofilms revealed a
                      significantly higher amount of biomass per volume filter bed
                      in the BAC filter bed than in the anthracite filter bed,
                      explaining the discrepancy in the bulk organics removal and
                      potentially the removal of degradable OMP such as valsartan.
                      The dominant taxa in the microbial communities were found to
                      be similar and appeared at comparable relative abundances on
                      both filter materials. Among them, several have been
                      associated with OMP biotransformation, especially
                      ammonia-oxidising bacteria and archaea. The beta-diversities
                      of the microbial communities significantly differed between
                      the two filter media, however, these differences could not
                      be directly linked to the improved OMP removal in BAC
                      filters. Disinfection with ozone was particularly effective
                      for vegetative bacteria such as the bathing water quality
                      indicators Escherichia coli and enterococci. Post-treatment
                      with deep-bed filters and CW significantly improved the
                      disinfection result of ozonation, especially for parameters
                      that were less ozone-susceptible (somatic coliphages,
                      Clostridium perfringens). This demonstrated the
                      complementing effect of the different disinfection
                      mechanisms of ozonation (chemical) and filtration
                      (physical). Just as the conventional bacterial parameters,
                      ozonation effectively inactivated antibiotic resistant
                      bacteria (ARB). However, antibiotic resistance genes (ARG)
                      remained mostly unaffected by ozone and could only be
                      significantly removed during post-treatment. A selection
                      process of bacteria with ARG by ozonation was not observed.
                      A regrowth during biological post-treatment was found for
                      the parameters intact cell counts (flowcytometry) and
                      Pseudomonas aeruginosa. Based on the results of this pilot
                      study and the current knowledge from literature, a design
                      approach was proposed that provides guidance for the
                      selection and dimensioning of the biological post-treatment
                      process. Mandatory treatment goals (removal of biodegradable
                      oxidation by-products and toxicity) and site-specific
                      optional treatment goals (e.g. phosphorus removal) were
                      defined as the main criteria for the selection of a suitable
                      process. The dimensioning approach focuses on carbonyl
                      compounds as suitable representatives of biodegradable
                      oxidation by-products and assumes first-order kinetics for
                      their biodegradation. It enables to calculate EBCT as a
                      function of the targeted removal of carbonyl compounds. The
                      design approach was exemplarily applied to a real WWTP. BAC
                      filtration with additional coagulant dosing was selected as
                      the most suitable process for the site-specific treatment
                      requirements. To reach an overall removal of 80 $\%$ for a
                      set of selected carbonyl compounds, an EBCT of 16 min was
                      determined. This EBCT and the respective filter surface area
                      were approx. 20 $\%$ higher than calculated with a common
                      practice design approach that solely relies on a maximum
                      hydraulic loading rate of 15 m/h. The comparison
                      demonstrates that EBCT-based dimensioning approaches are
                      essential for ensuring an efficient removal of oxidation
                      by-products in biological post-treatment.},
      cin          = {314110},
      ddc          = {624},
      cid          = {$I:(DE-82)314110_20140620$},
      typ          = {PUB:(DE-HGF)11},
      doi          = {10.18154/RWTH-2024-09636},
      url          = {https://publications.rwth-aachen.de/record/994980},
}