WATERSHED BIOGEOCHEMISTRY IN THE ANTHROPOCENE LAB
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Research


The Watershed Biogeochemistry in the Anthropocene Lab studies how anthropogenic activities have altered the cycling of nutrients and contaminants through watersheds, with a focus on linked biogeochemical cycles within socioenvironmental systems. We examine the fate, transport, and transformation of these elements and compounds within and between terrestrial and aquatic ecosystems. We also evaluate the implications this has for the people and animals that live in these landscapes. Our lab uses a variety of interdisciplinary tools to address these questions including fieldwork, labwork, and data syntheses and takes place locally, nationally, and internationally. We are guided by four overarching research questions:
  1. How does geochemical setting (e.g., geochemical properties of source material, geochemical processes) constrain the biogeochemical cycling of elements, and how is human activity altering these cycles?
  2. When and where on the landscape do control points (hotspots and hot moments) emerge?
  3. How does coupled elemental cycling impact the fate of individual nutrients and contaminants?
  4. How can we use biogeochemical data to create a risk landscape that guides management, mitigation, and conservation efforts to reduce harms posed to people and wildlife?

Below are some examples of research conducted in the lab.

Long-term trends of trace elements in boreal streams
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Human activities and global changes alter the movement of elements from the atmosphere to land and ultimately into streams, particularly in northern latitude regions. However, there is limited understanding of how altered environmental conditions impact trace element movement. Even though some trace elements form essential nutrients, others are toxic to humans and wildlife. Therefore, determining long-term patterns in these elements is important to understand their human and ecosystem health impacts. With funding from NSF and in collaboration with Yadu Pokhrel (MSU), Ryan Sponseller (Umea University), and Hjalmar Lauden (SLU), we are determining how shifting environmental processes impact the fate and transport of contaminants in boreal streams at the Krycklan Catchment in Sweden. We are examining long-term patterns of trace elements in streamwater, quantifying trends in their concentration, identifying the associated drivers, and predicting how the concentrations will vary in the future.

Transport and fate of mercury from illegal artisanal and small-scale gold mining activities
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In the process of illegal artisanal and small-scale gold mining (ASGM), mercury is added to soil and sediment to isolate gold. This mercury-gold amalgam is then heated to create pellets of gold, releasing the mercury into the atmosphere while mercury remaining in tailings is deposited onto the landscape as mining waste. As a result, ASGM represents the largest source of global anthropogenic mercury emissions, more so than coal combustion. With funding from NSF DISES and in collaboration with Heidi Hausermann (University of Michigan), Emmanuel Effah, Richard Amankwah (UMaT Ghana), and Edith Parker (University of Iowa), we are examining atmospheric mercury transport processes, mercury accumulation in soil, and mercury uptake in plants near ASGM activities in Ghana. We are also evaluating the resulting exposure risk for local communities. We are also continuing previous work to understand where and when there are control points for mercury deposition and mercury methylation in tropical forests and surface waters near ASGM in the Peruvian Amazon. We then use this information to determine human and wildlife exposure to mercury, as well as best practices for reducing mercury exposure risk.

Relationship between methane and methylmercury production in aquatic ecosystems
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Both methylmercury and methane are harmful and produced by aquatic methanogenic microbes. Yet these two contaminants are rarely measured or managed simultaneously in aquatic ecosystems. In collaboration with Kelly Aho (Michigan State), we are examining publicly available data to evaluate evidence for linked greenhouse gas and methylmercury production in waterbodies across the continental US. In collaboration with Meredith Holgerson (Cornell), Roxanne Razavi (SUNY ESF), and Evie Brahmstedt (NYS WRI), we are performing field and lab experiments to quantify rates of methylmercury and methane production in New York ponds, as well as to evaluate the efficacy of potential intervention strategies.

Tracing mercury dynamics following harmful algal blooms in New York lakes
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Harmful algal blooms are becoming increasingly common in freshwater ecosystems. While these algal blooms have detrimental consequences for human and wildlife health, it is also likely that they impact the cycling of contaminants within these aquatic ecosystems. Mercury is one contaminant of concern, with over 200 lakes throughout New York containing mercury fish consumption advisories. When mercury is converted microbially into methylmercury, it is toxic and can bioaccumulate. Methylmercury is formed under low oxygen environments, while harmful algal blooms lead to reduced oxygen availability in lakes. With funding from the New York State Water Resources Institute and in collaboration with the New York Department of Environmental Conservation, we are investigating how harmful algal blooms are altering methylmercury dynamics in New York lakes.

Implications of agricultural sulfur additions on the cycling of mercury
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With the implementation of the Clean Air Act and its Amendments, sulfur deposition (i.e., acid deposition) has drastically decreased. Today, the largest source of sulfur is from agricultural activity, where sulfur is added as a pesticide/fungicide, fertilizer, soil conditioner, and nutrient carrier. For example, vineyards in Napa Valley, California use sulfur to prevent powdery mildew infection. But sulfur leaches into nearby aquatic environments, which also have elevated mercury concentrations from historical gold mining. With funding from the USDA NIFA and in collaboration with Eve Hinckley (CU Boulder), Peter Weiss (UCSC), and Nettie Calvin (UCSC), we are examining the extent to which sulfur inputs from vineyards are impacting the microbial conversion of inorganic mercury to the bioavailable and toxic form of methylmercury. We are also examining how the global sulfur cycle has changed over the past few decades, the implications this has for plant nutritional needs as well as environmental consequences, and how we can better manage sulfur for a sustainable future.

Can selenium provide protection from mercury bioaccumuluation and toxicity?
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Mercury is a potent neurotoxin that can impact both humans and wildlife. Selenium, while an essential nutrient, can cause deformities in organisms when present in high concentrations. However, some studies suggest that when both mercury and selenium are present at elevated levels, selenium can reduce mercury methylation, bioaccumulation, and/or toxicity. We are investigating evidence for mercury and selenium interaction at the geochemical and microbial levels, as well as at base of the food web using field data collection, field and laboratory experiments, models, and literature syntheses.​

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