DOI: 10.6073/pasta/9f52cd07eca1716272ddb313736316b1
title: Soil solution chemistry data from long-term study plots

description: Baltimore Ecosystem Study Long-Term Study Plot Soil Metadata
      
      
          Participants
      
          Peter Groffman, Cary Institute of Ecosystem Studies
      
      
          Richard V. Pouyat, U.S. Forest Service
      
      
          Lisa Martel, Cary Institute Of Ecosystem Studies
      
      
          Introduction
      
      
      
          The Baltimore Ecosystem Study (BES) has established a network of long-term permanent biogeochemical study plots. These plots will provide long-term data on vegetation, soil and hydrologic processes in the key ecosystem types within the urban ecosystem. The current network of study plots includes eight forest plots, chosen to represent the range of forest conditions in the area, and four grass plots. These plots are complemented by a network of 200 less intensive study plots located across the Baltimore metropolitan area. See Baltimore's Vegetation Structure And Its Ability To Remove Air Pollutants And Sequester Carbon Dioxide, online: http://beslter.org/frame4-page_3b_02.html .
      
      
          Plots are currently instrumented with lysimeters (drainage and tension) to sample soil solution chemistry, time domain reflectometry probes to measure soil moisture, dataloggers to measure and record soil temperature and trace gas flux chambers to measure the flux of carbon dioxide, nitrous oxide and methane from soil to the atmosphere. Measurements of in situ nitrogen mineralization, nitrification and denitrification were made at approximately monthly intervals from Fall 1998 - Fall 2000. Detailed vegetation characterization (all layers) was done in summer 1998.
      
      
          Data from these plots has been published in Groffman et al. (2006, 2009) and Groffman and Pouyat (2009).
      
      
      
      
          Plot Locations and Characterizations
      
      
          In November of 1998 four rural, forested plots were established at Oregon Ridge Park in Baltimore County northeast of the Gwynns Falls Watershed. Oregon Ridge Park contains Pond Branch, the forested reference watershed for BES. Two of these four plots are located on the top of a slope; the other two are located midway up the slope.
      
      
          Four urban, forested plots were established in November 1998, two at Leakin Park and two adjacent to Hillsdale Park in west Baltimore City in the Gwynns Falls. One of the plots in Hillsdale Park was abandoned in 2004 due to continued vandalism.
      
      
          In May 1999 two grass, lawn plots were established at McDonogh School in Baltimore County west of the city in the Gwynns Falls. One of these plots is an extremely low intensity management area (mowed once or twice a year) and one is in a low intensity management area (frequent mowing, no fertilizer or herbicide use). In 2009, the McDonogh plots were abandoned due to management changes at the school.
      
      
          Two grass lawn plots were established on the campus of the University of Maryland, Baltimore County (UMBC) in fall 2000. One of these plots is in a medium intensity management area (frequent mowing, moderate applications of fertilizer and herbicides) and one is in a high intensity management area (frequent mowing, high applications of fertilizer and herbicides).
      
      
      
      
          Plot locations:
      
      
      
          Hillsdale 1: 39 deg 19 min 28.14"N, 76 deg 42 min 16.49 sec W
      
          Hillsdale 2: 39 deg 19 min 31.24"N, 76 deg 42 min 28.62 sec W
      
      
          Leakin 1: 39 deg 18 min 1.32"N, 76 deg 41 min 37.08 sec W
      
          Leakin 2: 39 deg 18 min 5.42"N, 76 deg 41 min 34.15 sec W
      
      
          McDonogh 1: 39 deg 23 min 44.31"N, 76 deg 46 min 19.26 sec W
      
          McDonogh 2: 39 deg 23 min 52.26"N, 76 deg 46 min 23.52 sec W
      
      
          Oregon top-slope - 1: 39 deg 28 min 51.11 sec N, 76 deg 41 min 22.50 sec W
      
          Oregon mid-slope - 1: 39 deg 28 min 51.32 sec N, 76 deg 41 min 18.24 sec W
      
          Oregon top-slope - 2: 39 deg 29 min 12.74 sec N, 76 deg 41 min 22.88 sec W
      
          Oregon mid-slope - 2: 39 deg 29 min 12.68 sec N, 76 deg 41 min 18.62 sec W
      
          Oregon upper riparian: 39 deg 29 min 9.03 sec N,  76 deg 41 min 15.86 sec W
      
          Oregon lower riparian: 39 deg 28 min 52.06 sec N,  76 deg 41 min 15.54 sec W
      
      
          McDonogh 1: 39 deg 23 min 44.31 sec N, 76 deg 46 min 19.26 sec W
      
          McDonogh 2: 39 deg 23 min 52.26 sec N, 76 deg 46 min 23.52 sec W
      
      
          UMBC 1: 39 deg 15 min 8.82 sec N, 76 deg 42 min 10.43 sec W
      
          UMBC 2: 39 deg 14 min 6.50 sec N, 76 deg 42 min 48.71 sec W
      
      
      
          Soil Solution Chemistry
      
      
          Soil solutions are collected using zero tension lysimeters of the design described by Driscoll et al. (1988) and tension lysimeters purchased from SoilMoisture Equipment Corporation. Three zero tension lysimeters at 50 cm depth, four tension lysimeters at 10 cm and another four tension lysimeters at 50 cm depth were installed in all eight forested plots in November 1998. Two zero tension lysimeters at 50 cm depth were installed in the McDonogh grass plots in May 1999 and in the UMBC grass plots in fall 2000 and spring 2001.  In June of 2010, four tension lysimeters at 10 cm depth were installed at the Oregon upper and lower riparian sites on the Pond Branch tributary.  
      
      
          All lysimeters are sampled every four to six weeks. Tension lysimeters are pumped to 70 centibars of soil suction using pumps from SoilMoisture Equipment Corporation. Pressure is allowed to equilibrate over a period of one to seven days before samples are collected. The lysimeters are pumped into a stoppered flask until dry. The stopper of the flask is fitted with an attachment for a 20 mL vial such that sample fills the vial and then overflows into the flask. The sample in the vial is used for chemical analyses while the overflow in the flask is measured for total volume. After one lysimeter has been sampled, the tubing through which the sample is pumped is rinsed with DI water and then with a small amount of sample from the next lysimeter before the vial is attached and sample for chemical analysis for that lysimeter is taken.
      
      
          At the BES laboratory samples are syringe filtered using 25mm Whatman GF/F filters. Samples are refrigerated at 4deg C and sent regularly to CIES for analysis. From 1999 until sept 2006, Concentrations of NO3- and NH4+ and PO4-  were quantified colorometerically with a flow injection analyzer.  Starting in Sept 2006 only NO3- and PO4- were analysed. 
      
      
      
          Literature Cited
      
      
          Bowden R, Steudler P, Melillo J and  Aber J. 1990. Annual nitrous oxide fluxes from temperate forest soils in the northeastern United States. J. Geophys. Res.-Atmos. 95, 13997 14005.
      
      
          Driscoll CT, Fuller RD and Simone DM (1988) Longitudinal variations in trace metal concentrations in a northern forested ecosystem. J. Environ. Qual. 17: 101-107 
      
      
          Goldman, M. B., P. M. Groffman, R. V. Pouyat, M. J. McDonnell, and S. T. A. Pickett. 1995. CH4 uptake and N availability in forest soils along an urban to rural gradient. Soil Biology and Biochemistry 27:281-286.
      
      
          Groffman PM, Holland E, Myrold DD, Robertson GP and Zou X (1999) Denitrification. In: Robertson GP, Bledsoe CS, Coleman DC and Sollins P (Eds) Standard Soil Methods for Long Term Ecological Research. (pp 272-290). Oxford University Press, New York 
      
      
          Groffman PM, Pouyat RV, Cadenasso ML, Zipperer WC, Szlavecz K, Yesilonis IC,. Band LE and Brush GS. 2006. Land use context and natural soil controls on plant community composition and soil nitrogen and carbon dynamics in urban and rural forests. Forest Ecology and Management 236:177-192.
      
      
          Groffman, P.M., C.O. Williams, R.V. Pouyat, L.E. Band and I.C. Yesilonis. 2009. Nitrate leaching and nitrous oxide flux in urban forests and grasslands.  Journal of Environmental Quality 38:1848-1860.
      
      
          Groffman, P.M. and R.V. Pouyat.  2009. Methane uptake in urban forests and lawns.  Environmental Science and Technology 43:5229-5235. DOI:  10.1021/es803720h.
      
      
          Holland EA, Boone R, Greenberg J, Groffman PM and Robertson GP (1999) Measurement of Soil CO2, N2O and CH4 exchange. In: Robertson GP, Bledsoe CS, Coleman DC and Sollins P (Eds) Standard Soil Methods for Long Term Ecological Research. (pp 258-271). Oxford University Press, New York 
      
      
          Robertson GP, Wedin D, Groffman PM, Blair JM, Holland EA, Nadelhoffer KJ and. Harris D. 1999. Soil carbon and nitrogen availability: Nitrogen mineralization, nitrification and carbon turnover. In:  Standard Soil Methods for Long Term Ecological Research (Robertson GP, Bledsoe CS, Coleman DC and Sollins P (Eds) Standard Soil Methods for Long Term Ecological Research. (pp 258-271). Oxford University Press, New York 
      
      
          Savva, Y., K. Szlavecz, R. V. Pouyat, P. M. Groffman, and G. Heisler. 2010. Effects of land use and vegetation cover on soil temperature in an urban ecosystem. Soil Science Society of America Journal 74:469-480.