Assessment of the Impact of a New Industrial Discharge on an Urban Wastewater Treatment Plant: Proposal for an Experimental Protocol

Abstract

Assessing the compatibility of industrial discharges with the biological process of a municipal wastewater treatment plant (WWTP) may represent a critical task. Indeed, either focusing only on chemical characterization or ecotoxicity tests designed to assess the impact on surface waters may lead to questionable or misleading conclusions. The feasibility of an industrial connection to the sewer should better take into account the features of the downstream WWTP, in particular by studying the potential effects on the biomass of that specific plant. With this aim, a multi-step experimental protocol applicable by water utilities has been proposed: (step 1) calculation of the flow rate/load ratio between industrial discharge (ID) and urban wastewater (WW); (step 2) analysis of the modified operating conditions of the biological stage; (step 3) experimental assessment of the impact of the ID on the WWTP biomass by means of respirometric tests. An application of this protocol is presented in this work as a case study, namely a new ID (average flowrate 200 m3 d−1) coming from an aqueous waste treatment plant (AWTP) to be connected to the public sewer. The integrated evaluation of results showed that no negative impacts could be expected on the downstream urban activated sludge WWTP (treating a flow rate of around 45,000 m3 d−1).

Impact of Nano–Sized Polyethylene Terephthalate on Microalgal–Bacterial Granular Sludge in Non–Aerated Wastewater Treatment

“…Despite the existence of PET recycling processes, a considerable amount of PET inevitably enters the WWTPs [17]. As a non-volatile solid, PET may adversely affect the rheological properties of sludge in WWTPs, and new industrial discharge processes in WWTPs have been proposed [18,19]. Previous studies have reported that PET powder, at a concentration of 200 mg/L, has a significant inhibitory effect on Scenedesmus sp., leading to increases in the concentrations of extracellular hydrogen peroxide and extracellular polymeric substances (EPS) in microalgae, and scanning electron microscope (SEM) images have shown that microalgae adhere to the surface of MPs and form heterogeneous aggregations [20].…”