Recipient Organization
UNIV OF CONNECTICUT
438 WHITNEY RD EXTENSION UNIT 1133
STORRS,CT 06269
Performing Department
Plant Science and Landscape Architecture
Non Technical Summary
Connecticut and southern New England is a densely populated urban/suburban corridor along the Atlantic Seaboard that contains a considerable amount of amenity turfgrasses. As a result of urbanization, considerable portions of the natural and/or agricultural vegetation in this region has been largely replaced with amenity turfgrasses as the preferred landscape, and used as lawns, parks, recreational areas, athletic fields, golf courses, and other outdoor activities on grass that is mowed on a frequent basis. This vegetation replacement is occurring in other regions as well, and is not trivial. It has been estimated that there are approximately 16 to 20 million hectares (40 to 50 million acres) of land in the continental United States managed in turfgrasses, with the most of this area managed as lawns. This is an area three times larger than any irrigated crop in the United States, and is expected to increase as urbanization follows population expansion. Even though a sizeable land area is identified as being dominated by turfgrass, this landscape vegetation has usually been overlooked or not thought of as an important sink for soil carbon sequestration. Recent research suggests that there is greater soil carbon sequestration in turf than was expected. However, information is lacking as to which turf management practice or combination of practices promote the greatest amount of soil carbon sequestration. This project will determine the changes in soil carbon occurring under different species of cool-season turfgrass lawns (Kentucky bluegrass, tall fescue, perennial ryegrass, creeping red fescue) mowed at different heights, with clippings removed or returned, and receiving varying amounts of nitrogen fertilizer. Nitrogen fertilization is a common practice that promotes green color and increased density of turfgrass. When plant-available soil nitrogen is low, adding nitrogen fertilizers should increase turf growth and density, thus leading to more soil carbon accumulation. However, applying nitrogen beyond needs of the turfgrass plant could accelerate the loss of soil carbon instead of the desired effect of increasing soil carbon sequestration rates. Soil organic matter breakdown from microbial decomposition might be accelerated by the surplus reactive nitrogen. Understanding the role of turf N fertilization, in relationship to other turf practices such as cutting heights and handling of clippings, on the carbon cycling and storage in urban/suburban landscapes will provide guidance for lawn management practices that maximize carbon sequestration potential in these landscape areas. Identifying turf management practices that increase soil carbon sequestration will have direct benefits to the environment and natural ecosystems because they will be beneficial for greenhouse gas mitigation and reducing the threat of nitrogen pollution of sensitive aquatic ecosystems. It is expected that specific practices or combination of practices will be identified by this project. Promotion of these practices to turf managers will result in more soil C accumulation, leading to a more sustainable lawn system.
Animal Health Component
(N/A)
Research Effort Categories
Basic
(N/A)
Applied
(N/A)
Developmental
(N/A)
Goals / Objectives
The overall objective of this project is to determine the changes in soil C occurring under different species of cool-season turfgrass lawns receiving varying amounts of N, mowed at different heights, with clippings removed or returned. Target Dates: Late-Summer 2011 - Establishment of turf plots and initial soil sampling. Winter 2011/2012 - Analysis of soil samples. Spring 2012 - Soil sampling; imposition of treatments; annual CRIS report. Summer 2012 -Continue treatment imposition and plot maintenance; analysis of spring soil samples; tissue sample collection; data summarization. Fall 2012 - Soil sampling; analysis of fall soil samples and tissue samples. Winter 2012/2013 - Analysis of soil and plant tissue samples; statistical analyses. This cycle of activities repeats until Fall 2016. Fall 2016 - Project ends; CRIS Termination Report; preparation and submission of manuscripts. Expected Outputs: It is expected that specific turf management practices, or combination of practices, will be identified that optimize soil C sequestration amounts or rates. This information will allow for better decisions regarding lawncare practices that result in the maximum potential for soil C sequestration in our urban/suburban landscape, leading to a more sustainable system. Expected outputs include analysis of experiment data; incorporation of results into the undergraduate and graduate teaching programs, mentoring of graduate students; presentation of results to landscape managers, governmental regulatory agencies, policy makers, environmental groups, and other scientists; turf industry field days that include the experiment site; web-based articles and information that describe and interpret results; publication of scientific peer-reviewed manuscripts.
Project Methods
Soil C sequestration will be assessed in the field with a 4 x 2 x 3 x 5 factorial experiment set out in a split-split-plot design with three replicates. 4 common turfgrass species [Kentucky bluegrass (Poa pratensis), tall fescue (Festuca arundinaceae), perennial ryegrass (Lolium perenne), and creeping red fescue (Festuca rubra)] will be main plots. Combinations of 2 clipping handling practices (removed or returned) with 3 cutting heights (5, 7.5, 10 cm) will be the sub-plot treatments, and 5 varying N rates (0, 10, 20, 30, 40 kg/ha/month during the growing season, May to November) as urea, will be the subsubplot treatments. These amounts of N will span the range of commonly applied N rates for lawns in our climate. Plot size will be 2 x 2 m. Grasses will be established on a newly-prepared seedbed so that changes in soil C storage beginning from establishment can be determined. Prior to treatment imposition at the beginning of the experiment, soil samples will be collected from two depths (0 to 10 cm and 10 to 20 cm) from each plot. Soil samples will be dried and sieved to pass a 2-mm sieve and analyzed for total soil C concentration. Following treatment imposition, soils will be sampled to the two depths at the end of the growing season (late October-early November in our climate), and at the beginning of the next growing season (mid April-early May) for a total of five growing seasons. Monthly samples of the aboveground biomass of the turf will be collected and bulked to provide a single yearly estimate, and this will be analyzed for total C content. Aboveground biomass collection will occur between 10 and 14 days after N fertilization to insure that optimum N uptake and assimilation has occurred to promote aboveground growth. Since clippings will be returned and removed, an estimate will be made of the C input from the aboveground plant parts. At the end of the growing season, thatch layer samples will be collected and analyzed for total C. With an estimate from plant tissue, thatch layer, and soil samples, a C budget will be constructed for each plot. Analysis of variance will determine differences between species, N rates, cutting heights, clipping management, and their interactions. Changes in soil C measurements with time will be determined using repeated measures analysis, with sampling date designated as the repeated measure. Information gained from the project will be distributed to and discussed with turf extension personnel and other turfgrass scientists. Identification of turfgrass practices that optimize soil C concentrations will be promoted through existing extension programs and through popular and trade industry publications or on-line sources, and through peer-reviewed scientific journals. Emphasis of these desirable turf management practices will be incorporated into the undergraduate and graduate teaching programs. Once specific practices or combination of practices have been indentified that optimize soil C, workshops for professional turf managers employing pre- and post-workshop surveys could be used to assess degree of adoption or changes in current practices that occur because of the new information.