


The Combined Activated Sludge-Anaerobic Digestion Model (CASADM) quantifies the effects of recycling anaerobic-digester (AD) sludge on the performance of a hybrid activated sludge (AS)-AD system. The model includes nitrification, denitrification, hydrolysis, fermentation, methanogenesis, and production/utilization of soluble microbial products and extracellular polymeric substances (EPS). A CASADM example shows that, while effluent COD and N are not changed much by hybrid operation, the hybrid system gives increased methane production in the AD and decreased sludge wasting, both caused mainly by a negative actual solids retention time in the hybrid AD. Increased retention of biomass and EPS allows for more hydrolysis and conversion to methane in the hybrid AD. However, fermenters and methanogens survive in the AS, allowing significant methane production in the settler and thickener of both systems, and AD sludge recycle makes methane formation greater in the hybrid system.
The research objective was to determine the short-term ecological toxicity of ozonation byproducts on seed germination of three distinct plant types (radish, lettuce, and grass) compared to untreated and uncontaminated soils. We hypothesize that the reduction of heavy hydrocarbon contamination in soil by ozone application will provide more suitable habitat for the germinating seeds. The effect of ozone treatment on seed germination and seedling quality was measured using ASTM standards for early seedling growth in conjunction with a gradient of potting soil amendments. Ozonation parameters were measured using established methods and include total petroleum hydrocarbons (TPH), dissolved organic carbon (DOC), and pH.
This study demonstrated the TPH levels fall up to 22% with ozonation, suggesting TPH removal is related to the amount of ozone delivered as opposed to the type of crude oil present. The DOC values increase comparably across crude oil types as the ozonation dose increases (from a background level of 0.25 g to 6.2 g/kg dry soil at the highest ozone level), suggesting that DOC production is directly related to the amount of ozone, not crude oil type. While ozonation reduced the mass of heavy hydrocarbons in the soil, it increased the amount of ozonation byproducts in the soil. For the three types of seeds used in the study, these changes in concentrations of TPH and DOC affected the species differently; however, no seed type showed improved germination after ozone treatment. Thus, ozone treatment by itself had a negative impact on germination potential.
Future research should focus on the effects of post-ozonation, long-term bioremediation on eco-toxicity. By helping define the eco-toxicity of ozonation techniques, this research can improve upon previously established ozone techniques for petroleum remediation and provide economic and environmental benefits when used for soil treatment.
Magnetic nanomaterials exist in the brain tissues of neurodegenerative patients, particularly those suffering from Alzheimer’s disease (AD). These nanoparticles likely originated as airborne particles small enough to penetrate human blood-brain barriers (BBBs), ultimately reaching AD brains and potentially inducing cellular oxidative stress, contributing to AD development. The mechanism leading to AD is still unclear, significantly limiting effective treatment and prevention strategies. Clarifying these mechanisms requires identifying potential sources and oxidative reactivity of submicron magnetic particles.The goal of my dissertation is to investigate magnetite nanoparticles from biogenic, anthropogenic, and commercial sources. I aim to reveal their heterogeneous nature and oxidative reactivity to induce cellular oxidative stress. I developed strategies to quantify magnetic particles and statistically compare their chemical composition, mineral structural, and oxidative reactivity. My research seeks to provide investigation strategies to study magnetic particles in cellular environments and pollution sources, which ultimately aims to reveal the particle relative abundance, particle size, elemental composition, and metal speciation of magnetic particles to inform and guide current AD researchers.
I achieved five research objectives guided by the overarching research goal. Firstly, I characterized urban pollution magnetic particles, discovering their mixed structure (~40% metallic iron, ~60% magnetite) containing trace metals like copper. This finding suggested a novel oxidative mechanism involving metallic iron and copper. Secondly, I developed an analytical workflow to identify airborne particles smaller than 200 nm capable of penetrating BBBs, quantifying their abundance and distinguishing chemical groups in environmental samples. Thirdly, I created a similar workflow for analyzing particles in biological samples, providing essential methodological recommendations. Fourthly, I compared single-particle analytical techniques, evaluating their strengths and limitations to guide future studies of heterogeneous particles. Finally, I compared biogenic magnetite with high-purity commercial magnetite, revealing enhanced oxidative reactivity due to impurity metals in biogenic forms rather than magnetite itself.
The five objectives allowed me to understand critical factors influencing cellular oxidative stress linked to neurodegeneration, highlighting impurities in magnetite particles as key contributors. These new findings provided a new insight to understand the role of the mysterious magnetic nanoparticles in the development of neurodegenerative diseases.