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  1. Abstract Practitioner Points

    Post‐anoxic EBPR can achieve effluent of <0.2 mgP/L and <12 mgN/L.

    The P:C and VFA:P ratios can be predictive for EBPR process monitoring.

    Post‐anoxic EBPR was enriched forNitrobacterspp. overNitrospiraspp. and also forParcubacteria, which is a putative fermenting heterotrophic organism.

    Post‐anoxic specific denitrification rates (20°C) ranged from 0.70 to 3.10 mgN/gVSS/h.

    BLASTn analysis of 16S rDNA PAO primer set was shown to be improved to 93.8% for Ca. Accumulibacter phosphatis and 73.2%–94.0% for all potential PAOs.

     
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  2. Abstract Practitioner points

    Wastewater carbon recovery via anaerobic digestion with combined heat/power production significantly reduces water resource recovery facility (WRRF) environmental emissions.

    Wastewater phosphorus recovery is of value; however, struvite production exhibits negative environmental impacts due to MgO2production emissions.

    Bioplastics production on imported organic‐rich agri‐food waste can diversify the WRRF portfolio.

    Dairy manure can be successfully integrated into a WRRF for bioplastics production without compromising WRRF performance.

    Diversifying the WRRF products portfolio is a strategy to maximize resource recovery from wastewater while concurrently achieving environmental sustainability.

     
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  3. null (Ed.)
  4. Abstract Practitioner points

    Evaluated alone τANexhibits no statistical effect on effluent phosphorus in an EBPR configuration.

    Increased PHA synthesis, associated with increased VFAs and/or extended τAN,enhances aerobic phosphorus removal.

    PHA synthesis normalized to VFA loading increased with τAN, suggesting fermentation in the EBPR anaerobic zone.

    Aerobic phosphorus uptake increases linearly with anaerobic phosphorus release, with the slope exceeding unity.

    Increased VFAs can be substituted for shorter anaerobic HRTs, and vice versa, to enhance EBPR performance.

     
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