This study is aimed to provide comprehensive evaluation and mechanistic understanding of the impact of process intensification techniques applied in main and side stream wastewater treatment on biosolids management in terms of anaerobic digestion enhancement, dewaterability improvement, odor mitigation, as well as phosphorus and nitrogen removal. The first part of this study was conducted to understand the effect of anaerobic digester solids retention time (SRT) on odor emission from biosolids. A kinetic model and inhibitory studies showed the emission of methanethiol (MT), a representative odor compound, was primarily determined by the dynamic concurrence of MT production from amino acid and utilization by methanogens in the course of anaerobic digestion. MT emission pattern follows a bell-shape curve with SRT in anaerobic digesters. However, for digested and dewatered biosolids, SRT ranging from 15 to 50 days in anaerobic digesters demonstrated insignificant effect on the odor emission from biosolids. In contrast, the peak odor emission was found to exponentially increase with both shear intensity and polymer dose applied during dewatering. The second part of this study investigated the impact of process intensification practices on sludge dewatering performance. The integration of high-rate activated sludge process and anaerobic digestion elevated the sludge orthophosphate level, leading to struvite scaling and dewaterability deterioration. Superior orthophosphate removal, significant improvement of sludge dewaterability, and favorable economics were achieved through sludge conditioning by cerium chloride. Continuous flow aerobic granulation technology offered significant process intensification of mainstream treatment trains. However, its impact on biosolids management was not studied. This study showed that there was little dewaterability difference between aerobic granular sludge and activated sludge when polymer was not added. However, about 75% polymer saving and improved dewatering performance were observed with polymer addition. When subjected to high shear, a greater dewaterability deterioration was observed for granular sludge than activated sludge. The last part of this study is focused on the impact of anaerobic digestion process intensification through thermal treatment including pre-pasteurization, thermophilic anaerobic digestion, temperature phased anaerobic digestion, and thermal hydrolysis pretreatment. Improved methane production, pathogen reduction, dewatering performance, and odor mitigation were observed with the involvement of these high-temperature processes. However, special cautions and measure should be taken during the start-up of these high rate processes as they are more liable to digester souring. In addition, the in-depth understanding of the mechanism of recalcitrant dissolved organic nitrogen formation during sludge thermal pretreatment was provided. / Doctor of Philosophy / This study is aimed to provide comprehensive evaluation and mechanistic understanding of the impact of process intensification techniques applied in main and side stream wastewater treatment on biosolids management in terms of anaerobic digestion enhancement, dewaterability improvement, odor mitigation, as well as phosphorus and nitrogen removal. The first part of this study was conducted to understand the effect of anaerobic digester solids retention time (SRT) on odor emission from biosolids. A kinetic model and inhibitory studies showed the emission of methanethiol (MT), a representative odor compound, was primarily determined by the dynamic concurrence of MT production from amino acid and utilization by methanogens in the course of anaerobic digestion. MT emission pattern follows a bell-shape curve with SRT in anaerobic digesters. However, for digested and dewatered biosolids, SRT ranging from 15 to 50 days in anaerobic digesters demonstrated insignificant effect on the odor emission from biosolids. In contrast, the peak odor emission was found to exponentially increase with both shear intensity and polymer dose applied during dewatering. The second part of this study investigated the impact of process intensification practices on sludge dewatering performance. The integration of high-rate activated sludge process and anaerobic digestion elevated the sludge orthophosphate level, leading to struvite scaling and dewaterability deterioration. Superior orthophosphate removal, significant improvement of sludge dewaterability, and favorable economics were achieved through sludge conditioning by cerium chloride. Continuous flow aerobic granulation technology offered significant process intensification of mainstream treatment trains. However, its impact on biosolids management was not studied. This study showed that there was little dewaterability difference between aerobic granular sludge and activated sludge when polymer was not added. However, about 75% polymer saving and improved dewatering performance were observed with polymer addition. When subjected to high shear, a greater dewaterability deterioration was observed for granular sludge than activated sludge. The last part of this study is focused on the impact of anaerobic digestion process intensification through thermal treatment including pre-pasteurization, thermophilic anaerobic digestion, temperature phased anaerobic digestion, and thermal hydrolysis pretreatment. Improved methane production, pathogen reduction, dewatering performance, and odor mitigation were observed with the involvement of these high-temperature processes. However, special cautions and measure should be taken during the start-up of these high rate processes as they are more liable to digester souring. In addition, the in-depth understanding of the mechanism of recalcitrant dissolved organic nitrogen formation during sludge thermal pretreatment was provided.

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Denna rapport presenterar resultat och analys av prestandan i ett pilotförsök om temperaturstegsrötning (TPAD). Pilotförsöket genomfördes på uppdrag av Käppalaförbundet. Resultaten jämfördes med en nedskalad mesofil process som simulerade den nuvarande fullskaliga rötningsprocessen på Käppala  avloppsreningsverk. Syftet var att utvärdera om TPAD kunde erbjuda fördelar jämfört med det mesofila systemet. TPAD har tidigare visat stor potential i pilotstudier och till viss del i fullskaliga implementeringar på avloppsreningsverk runt om i världen. Då prestanda och beteende vid rötningsprocesser dock är starkt beroende av lokal slamkomposition och processparametrar, behövdes en skräddarsydd pilotstudie för att utvärdera TPADs applicerbarhet vid Käppala avloppsreningsverk specifikt. Sammanfattningsvis visade TPAD något bättre metanutbyte än det mesofila kontollförsöket (MAD), och VSD ökade markant. Dessa fördelar erhölls trots den lägre totala retentionstiden för TPAD. Kvävemineraliseringen ökade dock också märkbart vilket potentiellt kan medföra ökade kostnader associerade med rening av kväve i rejektvattnet för avloppsreningsverket. Avvattningsprov på labbskala visade ett omfattande utsläpp av TSS i rejektvattnet efter det termofila rötningssteget. Detta förbättrades dock avsevärt (om än inte i samma utsträckning som MAD) efter det mesofila skedet. Mycket preliminära resultat indikerade att TPAD hade en utmärkt inneboende hygieniseringsförmåga tack vare det termofila skedet, och resulterade i ett slutgiltigt rötslam som uppfyllde hygieniseringsriktlinjer enligt Revaq. TPAD verkade uppvisa hög robusthet, utan någon uppenbar syrakollaps trots hög belastning i det termofila steget. Framtida stresstester föreslås för att tvinga fram en termofil syrakollaps, vilket skulle kunna ge en syra/gas-fasad TPAD, med potentiellt ytterligare ökad prestanda enligt mycket av den befintliga litteraturen. / This report analyzes the performance of a pilot scale temperature phased anaerobic digestion process (TPAD) undertaken on commission from the Käppalaförbundet wastewater treatment plant. Results from the newly initiated TPAD pilot were compared to those of a scaled down mesophilic process simulating the current full scale digestion used at Käppala, to evaluate whether TPAD could provide benefits over the mesophilic system. TPAD had previously showed great promise at pilot and full scale at other plants around the world, but given that anaerobic digestion performance and behavior are highly dependent on local sludge composition and process parameters, a bespoke pilot was needed to evaluate TPAD at Käppala WWTP specifically. In summary, the TPAD exhibited slightly better methane yields than the mesophilic control, and showed better removal of volatile solids. Such benefits were seen despite the lower overall retention time of the TPAD. Nitrogen mineralisation however also increased, potentially imposing increased costs associated with sludge liquor nitrogen purification. Dewaterability tests showed the thermophilic stage of TPAD releasing large amounts of problematic colloidal material, which however was reduced by the subsequent mesophilic stage. Preliminary results indicated the TPAD had an excellent inherent hygienization ability owing to the thermophilic stage, producing a final digestate which fulfilled Revaq hygienization guidelines. The TPAD also seemed to exhibit great robustness, with no acid collapse in the thermophilic stage apparent despite high loads and short retention times. Future stress tests are proposed to test an acid-gas phased TPAD, with potentially further increased performance as per much of the existing literature.