Research Interests

I have a wide range of research interests focused on understanding, protecting, and restoring the natural environment and the benefits humans get from healthy ecosystems. I am particularly interested in opportunities at the intersection of science and policy where science can inform policies and lead to solutions to environmental problems and more habitat conservation. These include the assessment and valuation of ecosystem services and I have worked with colleagues on incorporating ecosystem services into U.S. federal policies and programs (see for example, Polefka and Sutton-Grier 2016, Schaefer et al. 2015 and Sutton-Grier et al. 2014) as well as international policies (Howard and Sutton-Grier et al. 2017, Wylie et al., 2016). In my recent role as research faculty at University of Maryland and Ecosystem Science Adviser at the National Ocean Service, I focused on science to support coastal sustainability and resilience in the face of climate change.

Hybrid infrastructureOne effort I found particularly exciting was the opportunity to synthesize our understanding of the benefits provided by natural ecosystems, or hybrid infrastructure which combines natural and built features (as seen in the figure), to reduce the risks of coastal flooding and erosion from storms. The use of natural and hybrid approaches if of growing interest in the U.S. and globally and it is important to include these options in our coastal planning and decision making so that we have alternatives to simply building more and bigger sea walls along our coasts. The results of this research synthesis were published in the journal Environmental Science & Policy (Sutton-Grier et al. 2015), and this article won the 2016 Ecological Society of America "Innovation in Sustainability Science" Award. This research on natural and hybrid infrastructure to support coastal resilience is of braod interest, not just to coastal managers, but also has generated interest from the American Society of Civil Engineers, the Climate Change Business Journal, and the American Institute of Architecture. (figure credit: K. Crossett, NOAA)

MangroveOne of my primary efforts for the almost seven years I was at NOAA was to found and lead NOAA's Coastal Blue Carbon team. My expertise in wetland carbon cycling made me ideally suited to explore the science and policy opportunities for NOAA related to coastal blue carbon. I helped put together a website explaining coastal blue carbon, about how coastal habitats (seagrasses, salt marsh, and mangroves) sequester and store so much carbon, and about NOAA's interests in coastal blue carbon. My work on coastal blue carbon was featured in a recent epidsode of the Ocean Currents Radio Show. I also helped do an analysis of whether and how carbon services of ecosystems can be incorporated into U.S. federal policies which was published in Marine Policy (Sutton-Grier et al., 2014) and Coastal Management (Pendleton and Sutton-Grier et al., 2013) and a recent update on progress on incorporating carbon benefits into U.S. efforts (Sutton-Grier and Moore, 2016). I presented these findings at the Ecological Society of America at the 2013 conference. This work was also featured in the National Wetlands Newsletter. Working with a student, I also examined how blue carbon can be incorporated in international projects with the goal of conserving coastal ecosystems and supporting community livelihoods in developing countries (Wylie et al. 2016). The National Ocean Service also featured me in a podcast on Coastal Blue Carbon. And I am a co-PI on a NASA carbon monitoring grant which is working to develop a framework for using remotely sensed data to estimate coastal wetland carbon stocks. (photo credit: NOAA Office of Habitat Conservation)

At NOAA, I also had the opportunity to work on several additional projects related to valuing ecosystem benefits to people. For example, I collaborated on an effor to incorporate storm protection benefits into the U.S. damage assessment process (Wellman et al. 2017). I also examined the relationship between nature and biodiversity exposure and human health and well-being (Sandifer and Sutton-Grier et al., 2015) and you can view my ESA 2014 presentation on this study as well. Another study synthesized our understanding of how stressors in the environment (such as nutrient pollution or ocean acidification) decrease coastal and marine ecosystem services thereby having negative impacts on human health and well-being (Sandifer and Sutton-Grier, 2014). A fourth study synthesized the negative impacts of derelict fishing traps on target and non-target species and on habitats (Arthur and Sutton-Grier et al., 2014). The first study I co-authored with NOAA authors examined the jobs created through restoration projects (Edwards et al., 2012). All of these studies aimed to help inform policy and decision making in coastal conservation.

In my doctoral and postdoctoral research, I examined how environmental factors drive ecosystem functioning, particularly nutrient cycling, and how these processes are altered due to human environmental change. Of particular interest are the roles that soil conditions and plant species play in driving nutrient transformations and greenhouse gas production.

My research focused on three themes: 1) Coupling of soil-microbial functioning, 2) Plant diversity and microbial links to biogeochemical cycling, and 3) Plant-soil-microbial feedbacks to the restoration of ecosystem function.

Species growing in growth chamber Species growing in the growth chamber at SERC. In my postdoc at the Smithsonian Environmental Research Center (SERC), I examined how different plant species and plant traits impact freshwater wetland microbial competition and methane production. I determined that as belowground biomass increases which leads to an increase in the oxygen transported to the microbes in the soil, methane production decreases (Sutton-Grier and Megonigal, 2011). I also examined the impact plant carbon inputs to soil have on microbial respiration and decomposition of soil organic matter via a reciprocal soil transplant experiment (Sutton-Grier et al., 2011a). At the Nature Precedings website you can view the presentations I gave of some of these results at the Ecological Society of America conference in 2009 (plant carbon data) and 2010 (plant trait and methane data).

In my dissertation, I examined how plant species and soil conditions influence nutrient transformations in restored wetlands. I focused on wetlands because they are unique ecosystems that connect the terrestrial and aquatic portions of the landscape, providing exciting opportunities for studying nutrient transformations in heterogeneous environments. I specifically focused on nitrogen (N) and carbon (C) dynamics and the connections between the cycling of these two elements. To address the challenges of studying the complex relationships between plants, soils, microbes, and nutrient cycling, I combined greenhouse studies of plant physiology with field studies of soil processes to address questions that intersect biogeochemistry, ecosystem ecology, and restoration. 

I worked at two research sites for my dissertation research. I examined the importance of plant functional diversity on the nitrogen cycle in the Stream and Wetland Assessment and Management Park (SWAMP) in Duke Forest, Durham, North Carolina. In a second project I studied the role of soil organic matter amendments in the development of soil properties and microbial activity in a restored wetland in Charlotte, N.C. 

Biodiversity plots in July 2005 Duke Forest Biodiversity Site in July 2005. My biodiversity project combined a field study with a greenhouse study and my collaborator on this project was Justin Wright in the Duke Biology department. We measured plant traits in the greenhouse and then used those traits to calculate a measure of functional diversity to assess whether this measurement of diversity was more tightly linked to ecosystem functioning than the more traditional measure of diversity, species richness. See Funk et al. 2016, for a recent summary of how plant traits can help us understand ecological functioning.

Biodiversity plots Sept 2005.JPG Duke Forest Biodiversity Site in September 2005. Our main findings from this experiment are that plant functional diversity significantly influenced denitrification potential through its interactions with soil conditions; increasing plant trait diversity led to increased denitrificaiton potential but mainly at higher soil resource levels (Sutton-Grier et al., 2011b). I presented these results at the Biodiversity and Restoration symposium at ESA, 2007. Working with colleagues we also determined that plant trait diversity buffers changes in denitrification potential through changing seasons and environmental conditions (McGill et al., 2010) and that a diversity of traits are important for maintaining multiple ecosystem functions (Sutton-Grier et al., 2012). I presented these last findings at the Ecological Society of America conference August, 2012 (view presentation).


Charlottte June 2004.JPG Charlotte site in June 2004. At this site I examined how soil compost additions have affected soil properties and and microbial activity over three years since restoration. Based on my results from this study, compost can be used to increase soil macronutrients, specifically nitrogen and phosphorus, which can benefit plant growth. Compost amendments can also stimulate microbial activity since I found higher rates of denitrification in plots with more compost (Sutton-Grier et al., 2009).

Charlotte Cs 2004.JPG Charlotte site in September 2004. I also found that, even though the Charlotte and Duke Forest sites differ in many respects, both sites have similar soil ecosystem structure meaning that similar soil variables and relationships between soil variables can be used to predict denitrification potential at both sites. This suggests there are fundamental relationships between soil properties and microbial functioning that persist even when restored wetlands have very different histories and soil conditions. However, a similar soil ecosystem structure did not guarantee similar ecosystem functioning at both sites (Sutton-Grier et al., 2010).

Restoration activities at Duke Forest Duke Forest Restoration In Progress, 2005. I also had the opportunity to mentor a Master's student, Josh Unghire, on a research project examining the impacts of restoration activities on soil properties that influence microbial nutrient cycling. We determined that restoration activities decreased soil organic matter levels while increasing phosphorus levels, and homogenized their spatial distributions. Four years post-restoration, there were fewer organic matter "hot spots" which are important for biogeochemical cycling suggesting that microbial processing of nutrients in the restored site could be limited by the disturbance and homogenization that occurred during restoration activities (Unghire et al., 2011). (Photo credit: M. Ho)

To read more about my doctoral research, please see my dissertation online.


Wellman, E., A. Sutton-Grier, M. Imholt, and A. Domanski. 2017. Catching a wave? A Case Study on Incorporating Storm Protection Benefits into Habitat Equivalency Analysis. Marine Policy 83:118-125. DOI.

Polefka, S. and A.E. Sutton-Grier.  2016. Making ecosystem services part of
business as usual in federal governance.
  Frontiers in Ecology and Environment. 14(4):175. DOI.

Sutton-Grier, A.E. and A. Moore. 2016.  Leveraging Carbon Services of Coastal Ecosystems for Habitat Protection and Restoration.  Coastal Management.44(3):259-277. DOI.

*Wylie, L., A.E. Sutton-Grier, and A. Moore. 2016. Keys to successful blue carbon projects: Lessons learned from global case studies. Marine Policy. 65:76-84. DOI.

Funk, J.L, Larson, J.E., Ames, G.M., Butterfield, B.J., Cavender-Bares, J., Firn, J., Laughlin, D.C., Sutton-Grier, A.E., Williams, L. and J. Wright. Revisiting the Holy Grail: using plant functional traits to understand ecological processes. Biological Reviews. DOI.

Schaefer, M., E. Goldman, A. Bartuska, A.E. Sutton-Grier, and J. Lubchenco. 2015. Nature as capital: Advancing and incorporating ecosystem services in United States federal policies and programs. Proceedings of the National Academcy of Sciences. 112 (24):7383-7389. (also see the full issue on Nature as Capital)

Sutton-Grier, A.E., K. Wowk, and H. Bamford. 2015. Future of our Coasts: The potential for natural and hybrid infrastructure to enhance the resilience of our coastal communities, economies, and ecosystems. Environmental Science & Policy.51:137-148.

Sandifer, P.A., A.E. Sutton-Grier, and B.P. Ward. 2015. Exploring connections among nature, biodiversity, ecosystem services, and human health and well-being: Opportunities to enhance health and biodiversity conservation. Ecosystem Services. 12:1-15.

Sandifer, P. and A.E. Sutton-Grier. 2014. Connecting Stressors, Ocean Ecosystem Services, and Human Health.  Natural Resources Forum.  38:157-167.  DOI

Arthur, C., A.E. Sutton-Grier, P. Murphy, and H,. Bamford. 2014.  Out of sight but not out of mind: Harmful effects of derelict traps in selected U.S. coastal watersMarine Pollution Bulletin.

Sutton-Grier, A.E., A.K. Moore, P.C. Wiley, and P.E.T. Edwards. 2014. Incorporating ecosystem services into the implementation of existing U.S. natural resource management regulations: The case for carbon sequestration and storage. Marine Policy. DOI

Pendleton, L.H., A.E. Sutton-Grier, D.R. Gordon, B.C. Murray, B.E. Victor, R.B. Griffis, J.A.V. Lechuga, and C. Giri. 2013.  Considering “Coastal Carbon” in Existing U.S. Federal Statutes and Policies.  Coastal Management. 41:439-456. DOI

Edwards, P., A.E. Sutton-Grier, and G. Coyle*. 2012.  Investing in Nature: Restoring Coastal Habitat Blue Infrastructure and Green Job Creation.  Marine Policy. 38:65-71. DOI

Sutton-Grier, A.E., J. Wright, and C. Richardson. 2012.  Different plant traits affect two pathways of riparian nitrogen removal in a restored freshwater wetland. Plant and Soil. 365:41-57. DOI

Sutton-Grier, A.E. and J.P. Megonigal.  2011.  Plant species traits regulate methane production in freshwater wetland soils.  Soil Biology and Biochemistry 43:412-420. DOI

Sutton-Grier, A.E., J. Keller, R. Koch*, C. Gilmour, and J.P. Megonigal.  2011a.  Electron donors and acceptors influence anaerobic soil organic matter mineralization in tidal marshes.  Soil Biology and Biochemistry.  43: 1576-1583. DOI

Sutton-Grier, A.E., J. Wright, B. McGill*, and C. Richardson.  2011b. Environmental conditions influence the plant functional diversity effect on denitrification potential.  PLoS ONE 6(2): e16584. DOI

Unghire, J.M.*, A.E. Sutton-Grier, N. Flanagan, and C. Richardson.  2011.  Spatial Impacts of Stream and Wetland Restoration on Riparian Soil Properties in the North Carolina Piedmont.  Restoration Ecology 19(6):738-746. DOI 

McGill, B.M.*, A.E. Sutton-Grier, and J. P. Wright.  2010. Plant trait diversity buffers variability in denitrification potential over changes in season and soil conditionsPLoS One 5(7): e11618. DOI

Sutton-Grier, A.E., M. Kenney, and C.J. Richardson. 2010. Examining the relationship between ecosystem structure and function using structural equation modeling: A case study examining denitrification potential in restored wetlands. Ecological Modelling. 221:761-768. DOI

Sutton-Grier, A.E., M. Ho, and C.J. Richardson. 2009. Organic amendments improve soil conditions and denitrification in a restored riparian wetland. Wetlands. 29:343-352. DOI


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