Nanoparticles (NPs) are of significant interest due to their unique properties, such as large surface area and high reactivity, which have facilitated advancements in various fields. However, their increased use raises concerns about environmental impacts, including on wastewater treatment processes. This review examines the effects of different nanoparticles on anaerobic, anammox, aerobic, and algal-bacterial granular sludge used in wastewater treatment. CeO₂ and Ag NPs demonstrated adverse effects on aerobic granular sludge (AGS), reducing nutrient removal and cellular function, while anaerobic granular sludge (AnGS) and anammox granular sludge (AxGS) showed greater resilience due to their higher extracellular polymeric substance (EPS) content. TiO₂ NPs had fewer negative effects on algal-bacterial granular sludge (ABGS) than on AGS, as algae played a crucial role in enhancing EPS production and stabilizing the granules. The addition of Fe₃O₄ NPs significantly enhanced both aerobic and anammox granulation by reducing granulation time, promoting microbial interactions, improving granule stability, and increasing nitrogen removal efficiency, primarily through increased EPS production and enzyme activity. However, Cu and CuO NPs exhibited strong inhibitory effects on aerobic, anammox, and anaerobic systems, affecting EPS structure, cellular integrity, and microbial viability. ZnO NPs demonstrated dose-dependent toxicity, with higher concentrations inducing oxidative stress and reducing performance in AGS and AnGS, whereas AxGS and ABGS were more tolerant due to enhanced EPS production and algae-mediated protection. The existing knowledge gaps and directions for future research on NPs are identified and discussed.

Titanium dioxide nanoparticles (TiO₂ NPs) are extensively used in various fields and can consequently be detected in wastewater, making it necessary to study their potential impacts on biological wastewater treatment processes. In this study, the shock-load impacts of TiO₂ NPs were investigated at concentrations ranging between 1 and 200 mg L^-1 on nutrient removal, extracellular polymeric substances (EPSs), microbial activity in aerobic granular sludge (AGS), and algal-bacterial granular sludge (AB-AGS) bioreactors. The results indicated that low concentration (≤10 mg L^-1) TiO₂ NPs had no effect on microbial activity or the removal of chemical oxygen demand (COD), nitrogen, and phosphorus, due to the increased production of extracellular polymeric substances (EPSs) in the sludge. In contrast, the performance of both AGS and AB-AGS bioreactors gradually deteriorated as the concentration of TiO₂ NPs in the influent increased to 50, 100, and 200 mg L^-1. Specifically, the ammonia‑nitrogen removal rate in AGS decreased from 99.9 % to 88.6 %, while in AB-AGS it dropped to 91.3 % at 200 mg L^-1 TiO₂ NPs. Furthermore, the nitrate‑nitrogen levels remained stable in AB-AGS, while NO₃-N was detected in the effluent of AGS at 100 and 200 mg L^-1. Microbial activities change similarly as smaller decrease in the specific ammonia uptake rate (SAUR) and specific nitrate uptake rate (SNUR) was found in AB-AGS compared to those in AGS. Overall, the algal-bacterial sludge exhibited higher resilience against TiO₂ NPs, which was attributed to a) higher EPS volume, b) smaller decrease in LB-EPS, and c) the favorable protein to polysaccharide (PN/PS) ratio. This in turn, along with the symbiotic relationship between the algae and bacteria, mitigates the toxic effects of nanoparticles.

The increasing occurrence of microplastics and antibiotics in wastewater poses emerging challenges for biological treatment processes. Microalgal-bacterial granular sludge (MBGS) has emerged as an efficient algae-based biotechnology for wastewater treatment; however, its response to simultaneous exposure to these contaminants remains largely unexplored. Here, the effects of degradable polycaprolactone microplastics (PCL MPs) and sulfamethoxazole (SMX) were evaluated at 1 mg/L during granulation and long-term operation. PCL alone caused only minor changes, whereas SMX impaired granule stability and reactor performance. Under combined PCL + SMX exposure, the strongest deterioration was observed, including a 5.2% decrease in ammonium nitrogen (NH₄⁺-N) removal and a 48.9% decrease in phosphate removal relative to the control. Effluent nitrite nitrogen (NO₂^--N) and nitrate nitrogen (NO₃^--N) concentrations increased to 8.9 and 31.6 mg/L, respectively, under combined stress. These changes were accompanied by lower microbial activities, with the specific nitrate reduction rate (SNRR) and specific phosphorus uptake rate (SPUR) decreasing to 31.6 mg N/g mixed liquor volatile suspended solids (MLVSS) and 10.3 mg P/g MLVSS, respectively. Extracellular polymeric substances (EPS) analysis further showed depletion of tightly bound proteins. Microbial analysis revealed community restructuring under SMX-containing conditions (R3 and R4), including enrichment of Nakamurella (up to 36.5% in R3) and Micropruina (up to 18.9%), alongside a decline in polyphosphate-accumulating genera such as Microlunatus. Overall, MBGS showed resilience to PCL alone, whereas SMX (especially in combination with PCL) induced significant structural and functional instability.