Hydrogen sulfide production in the sewer network is the major cause for sewer corrosion and odour related issues. Iron (Fe) salt dosing is one of the efficient methods for sulfide control in the sewer network by precipitating the biologically formed sulfide to iron sulfide (FeS) particles. Though Fe salt is efficient in controlling sulfide, it requires continuous dosing that necessitates the search for alternative cheap sources.Meanwhile, water utilities are seeking an efficient management strategy for the discharge of sludge by-product from the drinking water treatment process. This byproduct also known as drinking water treatment sludge (DWTS) is either Fe-rich or aluminium (Al)-rich based on the coagulant used. The high Fe content in Fe-DWTS, could potentially be used to replace Fe salts for sulfide control in the sewer network.During Fe salt/Fe-DWTS dosing, formation of FeS particles is considered as the major sulfide control mechanism in the sewer network. Previous studies explored the multiple benefits of upstream sewer Fe dosing in the downstream processes such as phosphates removal in the bioreactor and sulfide mitigation in the anaerobic digester of the receiving wastewater treatment plant (WWTP). However, it is also well known that Fe salt is an effective coagulant for organic micropollutants (MPs) removal in the water treatment processes. As organic MPs such as pharmaceuticals, licit and illicit drugs, food additives etc., are ubiquitous in wastewater, the impact of dosing Fe salt/Fe-DWTS in the sewer network on the fate of these MPs is important but largely unknown. This thesis aims to address this research gap by investigating the impact of upstream Fe salt/Fe-DWTS dosing in sewers on the fate of organic MPs in the downstream sewer network and treatment process.Firstly, the impact of Fe salt dosing on the fate of selected organic MPs (8 compounds) was studied in a lab-scale rising main sewer reactor. The sulfide produced by sewer biofilms reacted with Fe 3+ forming black coloured FeS. Among the selected MPs, morphine, methadone and atenolol had >90% initial rapid removal within 5 min of Fedosing in the sewer reactor. The ultimate removal after 6 hr of retention time in the reactor reached 93-97%. Other compounds, ketamine, codeine, carbamazepine and acesulfame had 30-70% decrease of aqueous concentrations. The ultimate removal varied between 35 and 70% depending on their biodegradability. In contrast, paracetamol had no initial removal. Adsorption to the surface of FeS particles was likely responsible for the rapid MPs removal.
viii
Contribution by others to the thesisThis thesis contains some significant and substantial contribution from others as described below.