Browsing by Subject "Function"

Human welfare depends heavily on ecosystem services like water purification and nutrient cycling. Many of these ecosystem services, in turn, rely on reactions performed by microbes and yet remarkably little is known about how anthropogenic impacts are affecting the structure and function of microbial communities. To help address this knowledge gap, this dissertation uses field surveys and laboratory experiments to examine how watershed urbanization affects microbial communities in receiving streams. We focus on a specific functional group and its associated function - the denitrifying bacteria and denitrification. Denitrifying bacteria use reactive nitrogen and organic carbon as substrates to perform denitrification. Denitrification is one of the few ways to permanently remove reactive nitrogen from ecosystems. Since excess reactive nitrogen in water contributes to serious water quality and human health problems like toxic algal blooms and bowel cancer, denitrification in streams can be considered a valuable ecosystem service. Watershed urbanization, however, may alter the structure of denitrifying bacteria communities in ways that constrain their capacity to remove reactive nitrogen from streams.

Watershed urbanization leads to drastic changes in receiving streams, with urban streams receiving a high frequency of scouring flows, together with increased nutrient (nitrogen and carbon), contaminant (e.g., heavy metals), and thermal pollution. These changes are known to cause significant losses of sensitive insect and fish species from urban streams. Microbes like denitrifying bacteria may be similarly affected. In the first part of this dissertation, we describe results from four repeated surveys of eight central North Carolina streams affected to varying degrees by watershed urbanization. For each stream and sampling date, we characterized both overall and denitrifying bacterial communities and measured denitrification potentials. Differences in overall and denitrifying bacteria community composition were strongly associated with the urbanization gradient. Denitrification potentials, which varied widely, were not significantly associated with substrate supply. By incorporating information on the community composition of denitrifying bacteria together with substrate supply in a linear mixed-effects model, we explained 45% of the variation in denitrification potential (p < 0.001). Results suggest that 1) watershed urbanization can lead to significant changes in the composition of bacterial communities in streams and 2) such changes may have important functional consequences.

The second part of this dissertation examines how urbanization-driven changes to the structure of denitrifying bacteria communities might affect the way they respond to stress or disturbance. Some communities can resist changes to functionality in response to disturbance, potentially as a result of previous exposure and subsequent adaptation (legacy hypothesis) or high diversity (insurance hypothesis). We compare the resistance of two structurally distinct denitrifying bacteria communities to experimental disturbances in laboratory microcosms. Communities originated from either a polluted, warm urban streams or a relatively pristine, cool forest stream. In this case, the two communities had comparable compositions, but forest communities were more diverse than their urban counterparts. Urban communities experienced significant reductions in denitrification rates in response to the most severe increased pollution and temperature treatments, while forest communities were unaffected by those same treatments. These findings support the insurance, but not the legacy hypothesis and suggest that the functioning of urban streams may be more susceptible to further environmental degradation than forest streams not heavily impacted by human activities.

In the third part of this dissertation, we discuss results from a one-time survey of denitrifying bacteria communities and denitrification potentials in 49 central North Carolina streams affected to varying degrees by watershed urbanization. We use multivariate statistics and structural equation modeling to address two key questions: 1) How do different urban impacts affect the structure of denitrifying bacteria communities and 2) How do abiotic (e.g., temperature) versus biotic (denitrifying bacteria community structure) factors affect denitrification potentials in urban streams? Denitrifying bacteria community structure was strongly affected by the urban impacts measured. Community composition responded to increased temperatures, substrate supply, and contamination, while diversity responded negatively to increased temperatures and hydrologic disturbance. Moreover, increased temperatures and substrate supply had significant positive effects, while urbanization-driven changes to denitrifying bacteria community structure had significant negative effects on denitrification potential. The structural equation model captured 63% of the variation in denitrification potential among sites and highlighted the important role that microbial community structure can play in regulating ecosystem functioning. These findings provide a novel explanation for recent observations of decreasing denitrification efficiency with increasing urbanization. Ultimately, we hope findings from this dissertation will help inform more effective stream management and restoration plans and motivate ecologists to consider including microbial community structure in ecosystem models of microbe-mediated processes.

This dissertation seeks to bring together two philosophical literatures: the functions literature from the philosophy of biology, and the functionalist literature in naturalistic metaethics. Biological function suggests both objectivity and normativity: “the function of the heart is to pump blood” is an objective fact, and yet, hearts may malfunction—and malfunctioning is normative. Many ethicists wish to naturalize ethics—to help find a place for human normative lives in the objective natural world. In order to do so, they need tools to analyze humans as the products of evolutionary processes. Humans have a dual inheritance system involving both cultural and genetic inheritance that makes analysis of function for them particularly complex. In this dissertation, I develop a set of conceptual tools for those who wish to naturalize. I begin by developing an account of inheritance that can handle culture. Then, I elaborate the selected effects account of function so that it can handle all the evolutionary strangeness of culture. I then introduce the monolith fallacy—an error often committed by those studying human evolution—a tendency to oversimplify—to emphasize the high degree of complexity involved in any naturalizing project. Finally, I introduce the notion of value-guided functions—a kind of functioning not tied to our intentions, but to our values to round out the picture. I then apply the whole framework to the work of the functional metaethicists: Allan Gibbard, David Wong, Richard Joyce, and Philip Kitcher.

Sulfite oxidase, a metabolically important enzyme, catalyzes the physiologically critical conversion of sulfite to sulfate in the terminal step of the degradation of sulfur containing compounds. The enzyme has been the focus for much research since its discovery in the 1950's. A central question to understanding the mechanism of molybdoenzymes such as sulfite oxidase and nitrate reductase concerns the roles of active site residues and the coordination chemistry of the Mo atom in the structure and function of the enzyme. The goal of this work was directed towards the characterization and determination of the structures of active site variants of sulfite oxidase using a spectroscopic, kinetic, and protein crystallographic approach.

Earlier studies have identified a single, highly conserved cysteine residue as the donor of a covalent bond from the protein to molybdenum in sulfite oxidase and nitrate reductase. The C185S and C185A variants of chicken sulfite oxidase exhibited severely attenuated activity. Crystallographic and spectroscopic analysis of both variants revealed a change in the metal coordination, from a dioxo to a trioxo form of Mo.

Assimilatory nitrate reductase is a member of the sulfite oxidase family of molybdopterin enzymes. The crystal structure of the Mo domain of the enzyme from Pichia angusta revealed high structural homology in the active sites of nitrate reductase and sulfite oxidase. Both enzymes utilize the same form of the molybdenum cofactor and have three out of five residues conserved at the active site. Substitution of two active site residues in sulfite oxidase alters the substrate affinity of chicken SO from sulfite to nitrate, resulting in an increase of nitrate reductase activity over wild-type sulfite oxidase. Additionally we identified an additional amino acid position in sulfite oxidase that corresponds to a non-conserved position in NR that further increased NR activity. Finally, these nitrate reductase variants of sulfite oxidase were crystallized and the structures solved. This represents the first example of the transmutation of a molybdenum enzyme to change activity and substrate affinity to those of a homologous enzyme.