Abstract

Turfgrass cover in the U.S. is expanding because of increasing urbanization and the addition of approximately 675,000 ha of residential property every year. Despite its large-scale presence in the urban ecosystem, the role of turfgrasses in carbon (C) cycling in home lawns in southeastern U.S. soils has not been documented, and studies with warm-season turf grasses are lacking. The objective of this study was to estimate carbon (C) sequestration in soil as affected by turfgrass species, including: bermudagrass (Cynodon dactylon (L.) Pers. × C. transvaalensis Burtt Davy), centipede grass (Erecholmoa ophroides (Munroe) Hack.), and zoysiagrass (Zoysia spp.). The study was initiated in the winter of 2012 and conducted for two years on a loamy sand (fine-loamy, kaolinitic, thermic Typic Kanhapludult) soil. Eighteen lawns were sampled twice per year: six lawns of each grass species, with the harvested grasses separated into stems, above ground biomass (verdure) + thatch, and belowground roots. Soil samples (0 - 5, 5 - 10, and 10 - 20 cm) were also collected. Total C concentration was determined on finely ground-dried samples by combustion. Turfgrass species, season and years of sampling were all significantly (P ≤ 0.05) affected by C sequestration. Zoysiagrass had the highest mean levels of sequestered C, with a value of 5.54 ± 0.21, compared to 2.09 ± 0.11 and 4.23 ± 0.14 Mg·ha-1·yr-1 under bermudagrass and centipedegrass at the end of the study, respectively. This work indicates that turfgrass home lawns may be an important contribution to the global carbon sequestration level.

Highlights

  • Understanding the role of soils as a sink or a source for Carbon on a global scale is critical for evaluating changes in atmospheric carbon dioxide (CO2) concentration [1]

  • C sequestered in underlying soil was highest in zoysiagrass lawns and lowest in bermudagrass lawns

  • When soil C was summed for the three sampling depths zoysiagrass had greatest soil C, followed by centipedegrass, and bermudagrass

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Summary

Introduction

Understanding the role of soils as a sink or a source for Carbon on a global scale is critical for evaluating changes in atmospheric carbon dioxide (CO2) concentration [1]. Land use change can alter soil C pools and can have a significant effect on the C balance between soils and the atmosphere. Conversion of forest to row crops results in depletion of soil organic carbon (SOC) by an average of 35% [2]. Trumbore et al [3] found that when tropical dry forest in eastern Amazonia was converted to pasture, it lost an estimated value of 130 kg SOC ha−1·yr−1 from the top 10 cm of soil profile. The amount of organic C stored in soils varies with ecosystems and land use change [7]

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