Recent research in the agroecology lab shows that cover crop reduce nitrate leaching by as much as 56% compared to farms without cover crops. Check out the new article here!
My intern experiences this summer were nothing short of great. This summer, I helped Anna Kottkamp with her study of Delmarva Peninsula’s geographically isolated wetlands or Delmarva Bays. These wetlands are surrounded by upland and have no apparent surface water connectivity (Tiner 2003). Despite their geographic isolation, Delmarva Bays offer many ecosystem services such as providing habitat to many rare and endangered species (Sharitz and Gibbons 1982) and enhance local water quality (Phillips et al 1993).
With the lab and field work required to study these wetlands, I learned valuable skills that I can apply in my future career. One of these lessons is field preparedness. Whether your work is in the woods or in agricultural fields, or whether you are soil sampling or water sampling, fieldwork is an essential part of research and it comes with physical and environmental hazards. This guide is intended to share some things that I did right and some lessons I learned the hard way when it comes to field preparedness.
Phillips PJ, Denver JM, Shedlock RJ, Hamilton PA (1993) Effect of forested wetlands on nitrate concentrations in ground water and surface water on the Delmarva Peninsula. Wetlands Wetlands 13: 75-83.
Sharitz RR, Gibbons JW (1982) The ecology of southeastern shrub bogs (pocosins) and Carolina Bays: a community profile. FWS/OBS-82/04. US Fish and Wildlife Service, Division of Biological Services, Washington, DC
Tiner, R. (2003). Estimated extent of geographically isolated wetlands in selected areas of the united states. Wetlands, 23(3), 636-652.
-By Bianca Noveno
Salt-water intrusion (SWI) is a new challenge for farmers on the Eastern Shore. As sea levels continue to rise, more and more farm fields are becoming increasingly “salty,” often resulting in reduced and even complete loss of productivity. To make matters worse, there is evidence that salt accumulation also increases phosphorus loads to downstream waters. In the case of the Chesapeake Bay, this could reverse recent restoration efforts and hard fought water quality improvements.
Kate Tully, Keryn Gedan, and others are studying this problem; and their work aims to provide solutions that both help farmers and mitigate potential water quality degradation. Read more about their work in recent articles in NPR and The Atlantic.
This week, I helped Kate and Keryn install new groundwater wells at several of their sites. I had a great time and definitely learned a lot about agriculture on the Eastern Shore and salt-water intrusion. Below are a few pictures!
- By Nate Jones (postdoc at SESYNC)
At the AgroEcology lab, I primarily work with Josh Gaimaro on his research pertaining to cover crop use as a best management practice. Within my first two weeks of working in the lab, I was introduced to potassium chloride (KCl) extractions, which are one of the central procedures to his project. KCl extractions allow us to quantify the nitrogen concentration in soils, which helps model how the nitrogen moves through the soil, and how much of it gets taken up by plants or leached. Over the past two years, Josh collected over 1,000 samples, all which needed to be organized, weighed out, and extracted. Additionally, each sample required a replicate for quality control, which doubled the extraction count. When I was first introduced to the procedure, I did not understand the sheer quantity of samples I would need to process...
The first KCl extraction wasn’t perfect, even though Josh made the entire process look quick and effortless at first glance. The procedure is as follows: After weighing out a set of soil samples, we calibrated a pipette to dispense KCl into each tube. Afterwards, these samples are transferred to a shaker table, where they shake for an hour. In the meantime, you must prepare for the extraction which consists of setting up scintillation vials, placing funnels into them, and folding filter paper for each sample. Next, the tubes must go on a centrifuge to speed up filtering. However, we could only centrifuge 12 samples at a time, so it would take some time to get through all the samples. After the centrifuge, the samples are all filtered and organized once again.
The first extraction was around 75 samples, which wasn’t too intense since I was shadowing Josh and he was leading the procedure. Everything ran smoothly until the very end, where we were pouring the samples into the vials. We were using a shaky wooden device, which held the funnels a little above the vials, but didn’t secure the vials from moving. As I was pouring a sample, I accidentally knocked one over and it caused a domino effect! Three samples went down, and I was utterly embarrassed. Josh assured me that it is no big deal, and that we will redo these samples another day. Little did I know, I would do an extraction just like this at least twice a week at the minimum throughout the entire summer. The following day I was asked if I could do an extraction by myself with the help of another intern. Without giving it much thought, I replied “sure”, and began my journey of KCl extractions.
Once I got into the groove of things and familiarized myself with the procedure, I was averaging at 300 KCl extractions per day. This included the entire process- starting with weighing all the samples to cleaning up all of the dirty funnels and tubes. Little by little, I started working through these samples until the number of extractions left to do was zero. At first, the process didn’t seem to have an end, but somehow after three months of work, we finally finished the samples. Our last extraction was last Thursday, and was definitely bittersweet.
- By Christina Bychkov
Jones, D.L, Willett, VB. (2006) Experimental evaluation of methods to quantify dissolved organic nitrogen (DON) and dissolved organic carbon (DOC) in soil. Soil Biology and Biochemistry, 38:5: 991-999 https://doi.org/10.1016/j.soilbio.2005.08.012.
Murphy, D., Macdonald, A., Stockdale, E. et al. (2000) Biol Fertil Soils 30: 374. https://doi.org/10.1007/s003740050018
At 5:00 am on a Wednesday morning the sun has yet to rise in the Pocomoke River State Forest, but our team is already up cooking breakfast and putting on our boots to prepare for a day of work in the field. It’s important for us to get an early start in an attempt to beat some of the Maryland summer heat, or to make up for lost hours due to yesterday’s afternoon thunderstorm. We load up our truck with tape measures, augers, fertilizer, and of course our plants, switchgrass (Panicum virgatum) and saltmeadow corgdrass (Spartina patens). The purpose of this field excursion is to plant several salt tolerant crop species in order to see how they fare in the increasingly inundated and brackish farm fields of the eastern shore of Maryland, one of the regions most vulnerable to the effects of sea level rise in the entire country.
This summer I have been lucky enough to join the AgroEco Lab’s saltwater intrusion team and come along on multiple field excursions, where I have gotten to experience field work first hand and get a sense of what a typical day in the field looks like. Some may assume that scientists are only there to observe, and simply stand by making tick marks on their clipboards while others do the dirty work...but this couldn’t be further from the truth! One important thing I have learned this summer is that agroecologists are not afraid to get their hands dirty, and field work involves a great deal of manual labor, such a making soil “slushies” in order to install lysimeters, hammering probes 60 cm into the ground to get soil samples, and crawling up and down plots to plant our treatments.
During this planting excursion in particular I was thrown into the reality of field work: that it’s really hard! It involves long hours (sometimes dawn to dusk!), exposure to all kinds of weather, including sweltering heat and torrential downpours, strenuous labor, and worst of all, ticks! While some may know the eastern shore of Maryland for its picturesque landscapes of tall grasses blowing in the breeze against the backdrop of the Chesapeake Bay, or perhaps its delicious crab dinners, our field trips are certainly no vacation!
But sometimes these field excursions don’t seem like work at all, and the lines between work and leisure are more blurred. For instance, when I’m standing out on a wooden dock overlooking the bay, and behind me is a small cottage and willow tree that belong to a historic property, just down a dirt road from one of our field sites. Or when I get back from a long day in the field only to enjoy a lively make-your-own taco night with the rest of team, an evening fueled with laughter, stories, and an appreciation for good food. For all the things that make field work hard, there are plenty more that make it an incredible experience overall. As agroecologists we are lucky enough to get to go to so many extraordinary places and spend time outdoors, as well as get to bond with our fellow researchers, as a part of our job, which is a luxury not everyone has. I cannot wait to see all the places agroecology research will take me in the future!
- By Louisa Kimmell
Anderson, Eric K., et al. “Determining Effects of Sodicity and Salinity on Switchgrass and Prairie Cordgrass Germination and Plant Growth.” Industrial Crops and Products, vol. 64, Feb. 2015, pp. 79–87., doi:10.1016/j.indcrop.2014.11.016.
Titus, JG, and C Richman. “Maps of Lands Vulnerable to Sea Level Rise: Modeled Elevations along the US Atlantic and Gulf Coasts.” Climate Research, vol. 18, 2 Nov. 2001, pp. 205–228., doi:10.3354/cr018205.
If you have been around me in the lab for the last month, you might have caught me a few times watching a soccer game while scraping away soil samples. When there is a huge bin full of samples to scrape, you need something to pass the time. As a huge soccer fan, the World Cup brings me excitement every four years when it rolls around. Some of the countries I closely followed in this World Cup have players with great individual skill but have mostly gotten their nation to advance solely on team chemistry. So far, this observation has paralleled my experience in the Agroecology lab this summer.
I am working individually most days on Elizabeth de la Reguera’s project about how saltwater intrusion affects the storage of carbon in soil on agricultural fields. In this project, different soil aggregates are separated by sieving them from large to small particle size, until eventually silt and clay is left in the end. After the aggregates are dried in an oven, I weigh them and take them back to scrape in coin envelopes (shown in the picture). The amount of carbon is then tested after the samples are in envelopes. This work is important in observing how outside forces like saltwater intrusion can greatly affect aggregate stability . This research will hopefully help farmers take saltwater intrusion into account and seek solutions, such as establishing barriers to mitigate intrusion rate or adjusting crops to salt-tolerant species .
With the many individual projects the lab has, our “team chemistry” is still displayed. On a small scale, Elizabeth and I communicate well to ensure that her project is running smoothly. This can include relaying turkey tins to her car from the drying oven, needing more samples in the lab, or teaching me something new. In the field a couple weeks ago, I was part of a team of six when it came to installing lysimeters and soil sampling. We knocked out two fields in one day and got to go home a day early! On a large scale, the goal of our lab is to make agriculture more sustainable through research. We all know we aren’t making as much money as Messi or Ronaldo, but together we are definitely making an impact in the environmental and agricultural world. Even with the World Cup coming to an end soon, I still have a lot of great experiences left in the lab this summer.
-By Drew Mandich
USDA Natural Resources Conservation Service. (1996). Soil Quality Indicators: Aggregate
Stability. Retrieved from
Duan, Y. (2016). Saltwater intrusion and agriculture: a comparative study between the
Netherlands and China. TRITA-LWR Degree Project 2016:20.
We are interested in varying osmotic potentials because we want to know if crop death seen on saltwater intruded farm fields is due to the inability of plants to pull water out of the soil matrix or because of salt toxicity. This work will be complemented by another experiment of seed germination at varying sodium chloride (NaCl) concentrations in order to tease apart whether seeds are experiencing osmotic stress or ionic/salt stress.
This first year has been a year of logistics! Between field work on the lower eastern shore, to aggregate fractionation at the University of Maryland College Park, to seed germination experiments and George Washington University, I feel like the ring leader of a scientific circus. The second year can only be crazier and more exciting with all the data to analyze and a story to tell!
- By Elizabeth de la Reguera
Six, J., K. Paustian, E.T. Elliott, C. Combrink. 2000. Soil Structure and Organic Matter: I. Distribution of Aggregate-Size Classes and Aggregate-Associated Carbon. Soil Science Society of America Journal. 64:681-689.
Weil, R.R. and N.C. Brady. 2016. The Nature and Properties of Soils. 15th ed. Pearson Education, Columbus. ISBN: 9780133254488
This week, the Agroecology lab was all over the news!
A piece about our research on sea-level rise and saltwater intrusion aired on NPR's Weekend Edition. Check out the piece here.
Kate also presented at the Wilson Center on Sustainable water and resilient communities. Check out the webcast and news coverage at NewSecurityBeat.
Today marks the end of my time as an intern in the Agroecology Lab. I have been fortunate enough to spend the entirety of my senior year working in the lab with Dani Weissman and the other graduate students, Cullen McAskill the wonderful lab technician, and my fellow interns. Through my various research experiences in the lab, I have learned so much about biogeochemical cycling processes that impact agriculture, the importance of agroecology to integrate ecological and social approaches to agriculture, and standard chemical analysis research practices.
This semester I focused my efforts on a long-term research study to understand different nutrients, like nitrogen and phosphorus, that are dissolved and bound to soil particles in water samples taken from various agricultural plots on the Eastern Shore. Nitrogen in this form is formally called “Dissolved Organic Nitrogen” (DON), while other forms of nitrogen often found in the soil include nitrate and nitrite, which are necessary for plant growth. The agroecology lab is investigating these different forms of nutrients because it is important to understand how changing environmental conditions may impact the future of agriculture. Rising sea levels, for example, is causing saltwater from the ocean to intrude into agricultural plots on the Eastern Shore. This alters the chemical and biological processes that take place in agricultural soils (Osburn, 2016; Weston, 2006). To understand how nutrient forms have been changing over time in response to saltwater intrusion, I conducted digestion experiments on water samples to specifically target dissolved organic nutrients. Essentially, the experiment required me to add various chemicals to the water samples (as shown in Figure 1) and then run them through an autoclave, which heats the samples up to extremely high temperatures. This breaks up any bonds between the nutrients and dissolved soil components to isolate the nutrients to be further analyzed.
The results of this experimental digestion process will provide important information on plant nutrient availability once they undergo a next step of further chemical analysis. It is a good feeling to be able to contribute to the research findings of the Agroecology Lab. I will sorely miss my time working there now that the semester has come to a close, but I will be forever grateful to all that I have learned and for how it has changed my perspectives of agroecology.
Osburn, Christopher L., Lauren T. Handsel, Benjamin L. Peierls, and Hans W. Paerl. 2016. “Predicting Sources of Dissolved Organic Nitrogen to an Estuary from an Agro-Urban Coastal Watershed.” Environmental Science & Technology, 50: 8473-8484.
Weston, Nathanial B., Ray E. Dixon, and Samantha B. Joyce. 2006. “Ramifications of increased salinity in tidal freshwater sediments: geochemistry and microbial pathways of organic matter mineralization. Journal of Geophysical Research, 111: G01009.
- By Alexis Boytim
I am Jonathan Moy, an undergraduate intern in the Agroecology lab. I work with Elizabeth de la Reguera, an MS student here, in two of her projects. Her work is largely on how saltwater intrusion in Maryland affects the carbon found in soil. We recently finished transferring four thousand switchgrass plants to UMD’s greenhouse. Later in the year, the lab will be planting the switchgrass along with other salt-tolerant plants in saltwater intruded agricultural plots to determine the carbon the plants imparted in the soil. The data from that experiment will be helpful in giving farmers in Maryland a well-supported reason to use salt-tolerant crops in their crop rotations. The project I am working on right now examines the aggregate distribution in saltwater intruded agricultural fields. Soil aggregates are important to the available nutrients to the soils . We are most closely looking at soil carbon—thus the title of this post. Carbonation the way most people use it usually refers to carbon dioxide reacting with a beverage to make it effervescent. While that doesn’t happen in our soils, carbon is still very interesting in soils! The method we are using uses a series of sieves to separate the soil carbon by availability [2,3]. Essentially, the smaller the aggregates are, the less available the carbon is to the plants’ roots . One of the pictures with this post shows Elizabeth displaying the second smallest sieve we use in this experiment. Fun fact: the picture also features the very first sample we processed for this experiment.
During spring break, I was given the opportunity to visit the sites that we are working on! You may not be able to tell from the picture (I’m the guy in blue), but I had a blast soil sampling. If you look really closely, you can see that I’m smiling. Those soils were the same soils that we are processing right now, so that is just one more thing to be excited about when processing my samples. Before that, I spent a lot of time in the Greenhouse seeding, thinning, and transferring switchgrass until we had four thousand switchgrass plants individually growing in deep planting plugs.
- By Jonathan Moy
Ontl, T.A. et al. (2013). Topographic and Soil Influences on Root Productivity of Three Bioenergy Cropping Systems. The New Phytologist, 199, 727-737. doi: 10.1111/nph.12302
Elliott, E.T. (1986). Aggregate Structure and Carbon, Nitrogen, and Phosphorus in Native and Cultivated Soils. Soil Science Society of America Journal. 50, 627-633.
Six, J. et al. (2000). Soil Structure and Organic Matter: I. Distribution of Aggregate-Size Classes and Aggregate-Associated Carbon. Soil Science Society of America. 64, 681-689.