2022
DOI: 10.3390/en15197251
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Energy Consumption for Nutrient Removal from High-Nitrate and High-Phosphorus Wastewater in Aerobic and Anaerobic Bioelectrochemical Reactors

Abstract: An attempt was undertaken to determine indicators of energy consumption in bio-electro reactors (BERs) i.e., an aerobic rotating electrobiological disc contactor (REBDC) and an anaerobic sequencing batch biofilm reactor (SBBR), during contaminant removal from soilless tomato cultivation wastewater having a specific composition, i.e., high nitrate and phosphorus concentrations and low COD. Because of this specificity, the energy consumption during the treatment process was characterized by a cumulative indicato… Show more

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Cited by 5 publications
(8 citation statements)
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References 55 publications
(115 reference statements)
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“…The electrical energy generated in the form of a direct electric current could also be harnessed in DW electrocoagulation or in the bioelectrochemical treatment stage. The usefulness of both direct and alternating current in DW treatment has been confirmed in previous studies [32].…”
Section: Electrical Energy Productionsupporting
confidence: 63%
See 1 more Smart Citation
“…The electrical energy generated in the form of a direct electric current could also be harnessed in DW electrocoagulation or in the bioelectrochemical treatment stage. The usefulness of both direct and alternating current in DW treatment has been confirmed in previous studies [32].…”
Section: Electrical Energy Productionsupporting
confidence: 63%
“…Electric current consumption using the Rotating Electrobiological Disk Contactor ranged from 118 to 2170 kWh/kgN (removed nitrogen) and from 104 to 9456 kWh/kgP (removed phosphorus) depending on the electrical current density (from 0.62 to 10.0 A/m 2 ) and the wastewater hydraulic retention time (from 4 to 24 h). In the case of another solution, namely Sequencing Batch Biofilm Reactor, the energy consumption ranged from 49 to 144.5 kWh/kgN (removed nitrogen) and from 82 to 787 kWh/kgP (removed phosphorus) depending on the electric current density used (0.62-5.0 A/m 2 ) at HRT 1d [32]. At the same time, DW is effectively pre-treated upon the precipitation of mainly phosphorus with calcium and magnesium ions already at pH > 7.5 [33].…”
Section: Introductionmentioning
confidence: 99%
“…The numbers indicate that up to 50% of the total energy supplied in a conventional WWTPs is used to satisfy the aeration demand for carbon and nitrogen oxidation processes (Gude et al 2015 ; Ghimire and Gude 2019 ). Another study suggests that the contribution of biotreatment processes to total electric power consumption may reach up to 80% (Rodziewicz et al 2022 ). In fact, it is expected that its consumption will be higher in the future due to the increase in pollutant load and stringent environmental regulations (Wang et al 2019 ).…”
Section: Comparison Of Power Demand Among Biological Treatment Proces...mentioning
confidence: 99%
“…Likewise, the external carbon sources for the denitrification process can lead to operating costs of up to € 3.64/kg N removed (Arias et al 2018 ). In a typical WWTP with nitrification-denitrification, the energy consumption can reach 14.6 kWh/kg N removed (Panepinto et al 2016 ; Wang et al 2019 ; Rodziewicz et al 2022 ). In a simulation model, energy consumption during N removal can reach 52 kWh/kg N removed using indicators for loads of total nitrogen removed from dairy wastewater in biological processes (Żyłka et al 2021 ).…”
Section: Comparison Of Power Demand Among Biological Treatment Proces...mentioning
confidence: 99%
“…The course and efficiency of many of them depends on the presence of intermediate or final products of processes which commenced at the beginning of the cycle. Most of these processes are affected by the current flow between the electrodes [23]. The literature presents data on the operation of bio-electrochemical reactors, in which the current is supplied during the entire cycle [9,[12][13][14][15][16][17].…”
Section: Introductionmentioning
confidence: 99%