Abstract
The prevalence of deep root systems on urban trees has been well documented, but the consequences are not well understood. The relationship between structural root depth and vigor of street trees was investigated in Greensboro, North Carolina; Snoqualmie, Washington; and Glen Ellyn, Illinois, United States. Regression analysis was used to explore the relationship between root depth and crown vigor, trunk diameter growth, and trunk condition as indicators of tree performance. The average depth of structural roots for most species was less than three centimeters. However, in 10 of the 14 species included in the study, the structural roots of 20%–60% of the individual trees were more than eight centimeters deep. Regression analysis showed a significant relationship between root depth and indicators of tree performance for Acer rubrum, Quercus bicolor, Fraxinus oxycarpa, and Tilia cordata, but no relationship was identified for other species measured. Root depth explained less than half of the reduction in tree performance of these species, however, and is apparently only one of several factors affecting the growth of street trees.
Excessively deep root systems are common on trees in urban and suburban landscapes. The structural woody roots that collectively form the root flare have been found to be more than 7.6 cm below the soil surface on up to two-thirds of street trees in several Illinois and Minnesota, U.S., cities (Watson et al. 1990; Giblin et al. 2006). In Long Island, New York, U.S., the average depth of soil over the structural roots was slightly more than 15 cm (Smiley 2006). This is deeper than the best management practice (BMP) recommendation that “at least two structural roots should be within 2.5 to 7.6 cm of the soil surface” (Watson and Himelick 2005).
In addition to simply planting trees too deeply in the landscape, nursery field production practices can also contribute to deep root systems (Harris et al. 2001; Hewitt and Watson 2009). In the 1980s, deep roots were reported on New York City, New York, U.S., trees and were attributed to nursery practices prior to planting (Berrang et al. 1985). In a study of Ohio, U.S. nurseries, the average depth of structural roots in nursery fields and harvested root balls has been reported at 2–10 cm and 7–11 cm, respectively (Rathjens et al. 2007).
The question of how the deep root systems are affecting tree performance has not been adequately answered. Controlled experiments in field plots showed that deep root systems reduce survival and growth under some conditions, especially poor drainage (Wells et al. 2005; Arnold et al. 2005; Arnold et al. 2007; Bryan et al. 2010; Day and Harris 2008). Similar studies are lacking on trees planted in urban and suburban landscapes where many factors can affect tree growth and vigor. This study attempts to understand whether root depth affects vigor of commonly planted street trees in Greensboro, North Carolina (NC); Snoqualmie, Washington (WA); and Glen Ellyn, Illinois (IL).
METHODS
Arborists were contacted to locate suitable street tree plantings for the study. Knowledge of site history and consistency in site conditions were important considerations. Tree inventory records were examined from nine locations, six were visited for evaluation, and three were chosen.
Study Sites
Sites were chosen based on their geographic and climatic differences, species and number of trees available, and availability of local cooperators. The NC site was a large commercial property where the space between the pedestrian sidewalk and street curb was less than two meters wide and too narrow for planting. Therefore trees were planted one meter from the sidewalk on the side away from the street with 10 m or more open space beyond. A single cultivar of (Acer rubrum) trees was growing along the entire street.
The WA site was a residential neighborhood. Planting space width between the pedestrian sidewalk and street curb was somewhat variable from street to street but was typically less than two meters. A single species or cultivar was planted along each street. Streets with Quercus rubra, Fraxinus oxycarpa, and Tilia cordata were used in the study.
The IL site also consisted of street trees in a residential neighborhood. Planting space was also of variable width. Plantings along each street were of mixed species. When there were insufficient numbers of trees of a species for valid data analysis, the data were reported by genus. All trees were considered well-established. Trees in NC and WA were all planted as a group at the same time, 5 to 10 years earlier, but the exact year of planting was not available from records.
All trees were planted as ball-and-burlap stock, and trees were surrounded by turfgrass beyond a small (1–1.5 m) mulch ring at the base of the tree. Sampling dates and species for each site are listed in Table 1.
Root Depth
The root flare is the commonly used reference point for root depth discussions, but is really a zone rather than a specific point that can be measured precisely. To be more specific in this study, and in compliance with best management practices (Watson and Himelick 2005), root depth was measured from the upper surface of individual roots at the point where the root became distinct from the trunk. Depth was measured to the nearest half-centimeter relative to the soil against the trunk. The depth of individual roots usually varied around the tree. The depth of the two uppermost woody structural roots was recorded for each tree and averaged. If the soil against the trunk was higher or lower than the surrounding grade, this measurement was recorded and root depth relative to surrounding grade was calculated.
Root collars were excavated with hand tools and pneumatic excavation, depending on circumstances at each site. At WA, hand digging was the only option, and root collars were excavated to a maximum depth of 20 cm. Further hand excavation would have caused more site disruption than was tolerable. If no roots were found within 20 cm, depth was recorded as >20 cm. At IL, root collars were first excavated by hand to a depth of 15 cm, and if roots were not exposed, a pneumatic excavation tool was used on a return visit to excavate until roots were located.
At the NC site, root collars had been excavated several months earlier to expose the structural roots because Phytophthora lesions were discovered on the lower portion of the trunk (pers. comm.: E. Thomas Smiley). The depressions were filled with coarse mulch that was easily removed by hand to re-expose the structural roots.
Tree Performance
A visual rating system was developed for crown vigor. Trees were rated during the dormant season at WA, and only twig growth could be rated.
Vigor ratings:
1 – Vigorous: Terminal twig growth; leaf size and color better than average for species.
2 – Normal: Terminal twig growth; leaf size and color typical of species.
3 – Acceptable: Terminal twig growth; leaf size and color less than typical, but acceptable.
4 – Stress overcome: History of subnormal twig growth or minor twig dieback, but now acceptable or better.
5 – Current stress: Subnormal twig growth; leaves small, scorched or off color; minor dieback.
6 – Significant dieback: Major portions of crown dead, still in decline.
7 – Replacement needed: Dead or nearly so.
In addition to crown evaluations, trunk condition was also rated at the North Carolina site. This tree–health variable was included because these trees had a history of Phytophthora lesions on the lower portion of the trunk. The scale was based on visual estimation of the portion of the trunk circumference damaged by the disease lesion: 0 = 0%, 1 = 1%–25%, 2 = 26%–50%, 3 = 51%–75%, 4 = 76%–100%.
Trunk diameter was measured with a diameter tape 15 cm above soil line prior to excavation. Trunk diameter was used to assess performance only on sites where trees of uniform size, from the same source, were all planted at the same time (NC, WA).
Statistical Procedures
Regression analysis was used to examine the relationship between root depth and tree performance, with depth as the independent variable, and crown vigor, trunk condition, or trunk diameter as the dependent variable. Linear regression was used for trunk diameter measurement data (SAS procedure PROC REG, SAS 9.2). Significance is reported for P < 0.05. Crown vigor and trunk condition ratings were analyzed with logistic regression (SAS procedure PROC LOGISTIC, SAS 9.2) with Somers’D used as an indicator of model fit. Significance is reported at χ2 probability P < 0.05.
RESULTS AND DISCUSSION
Root depth showed high variability on all sites. Only Fraxinus oxycarpa and Tilia cordata structural root depth averaged greater than 7.5 cm, the maximum depth recommended by best management practices (Watson and Himelick 2005). The average depth of the structural roots was less than 3 cm for most species. The range of root depths may reflect the situation more meaningfully. The range of uppermost structural root depth of individual trees was in excess of 20 cm for most species. Within that broad range, the shallowest roots of 20%–60% of the individual trees were more than 7.5 cm deep in 10 of the 14 species included in the study (Table 1). This agrees with previous studies where similar numbers of trees with roots more than 7.6 cm deep were reported (Watson et al. 1990; Giblin 2006).
Regression analysis showed a significant relationship between root depth and tree performance for some species. Increasing root depth did accompany at least one measure of tree performance in four species (Table 2; Figure 1). Crown vigor and trunk condition of Acer rubrum decreased with increasing root depth at NC. Crown vigor was reduced in Quercus bicolor for IL, but not for any of the other species evaluated at the same site. Trunk diameter growth of Fraxinus oxycarpa and Tilia cordata was reduced at WA, but there was no relationship evident for Q. rubra. It was not within the scope of this study to determine what specific soil conditions may have been responsible for reducing the growth and vigor of trees with deep root systems.
Species generally considered highly tolerant of urban landscape conditions (Gilman 1997; Dirr 2009) showed no significant relationship between root depth and condition. These include Fraxinus sp. (F. pennsylvanica and F. Americana cultivars are both commonly grafted on F. pennsylvanica root stock), Acer × freemani, Malus sp., Gymnocladus dioica, Taxodium distichum, Ulmus hybrid (often grafted onto Ulmus pumila root stock). These species are planted frequently in urban areas because they can tolerate a wide variety of conditions, including deposition of soil over the roots in flooding events in nature. These species proved to be the most capable of tolerating deep root systems. Q. rubra and Quercus sp. (primarily Q. macrocarpa and Q. muehlenbergii), generally considered moderately tolerant of urban site conditions, were also unaffected by root depth. Maximum root depth of Gleditsia triacanthos was 4.5 cm, which is within the BMP guidelines for root depth (Watson and Himelick 2005) and understandably this species showed no relationship between root depth and tree performance.
Crown vigor was not related to root depth for any species on the WA site. The coastal regions in the Pacific Northwest are known for their nearly ideal growing conditions. The WA site was at an elevation of 243 m in the Cascade Mountains. Average high temperature during the summer months is 7°C cooler than the other two sites (22°C versus 29°C) (www.intellicast.com). Symptoms of stress or dieback may be less likely to develop when above ground conditions are less stressful, even if root system function is reduced by a deep root system. Trunk diameter growth was reduced on two of the three species (Table 2), possibly reflecting overall lower performance, though crown appearance was acceptable.
At most, root depth could explain less than half of the reduction in crown vigor, trunk condition, or trunk diameter growth. Root depth is only one of several factors affecting tree performance on street tree plantings. Soil conditions, seedling rootstocks, and installation and maintenance procedures on street tree planting sites can be highly variable, even within an apparently uniform planting on the same street. High variability in non-experimental field plots compared to their more controlled counterparts can make potential effects of deep root systems on tree vigor difficult to discern.
CONCLUSIONS
These results show that deep root systems are not causing widespread decline and losses to urban trees in the first ten years after planting. There was a significant relationship between root depth and tree performance for only some species, explaining less than half of the reduction in any indicator of performance. Most of the species included in this study were considered at least moderately tolerant of adverse conditions. Deep roots may have a greater effect on more sensitive species. Even a modest reduction in vigor could be serious for species that find it challenging to grow in urban landscapes, and for many moderately sensitive species on very difficult sites.
The range of data collected in this initial study was limited. Information on a wider variety of species is needed. Given the accepted variability of soils on urban sites, more information on site soil conditions could improve researchers’ understanding of which factors are most affecting tree performance.
Though the reduction of tree performance due to deep roots was modest, the problem may be so widespread that there could still be a significant impact on the urban forest as a whole. When all species are combined, the structural roots were at least 8 cm deep on 26% of the trees. Growth and vigor is being reduced in some cases by as much as 50%. The potential reduction in ecosystem services provided by these underperforming trees over their lifetime could be substantial.
Acknowledgments
This study was funded in part by a grant from the USDA Forest Service Urban and Community Forestry Program on the recommendation of the National Urban and Community Forestry Advisory Council. Cooperators providing invaluable assistance at the study sites were E. Thomas Smiley, Liza Holmes, and Elizabeth Schulte of Bartlett Tree Research Laboratories; Jim Barbarinas, Urban Forestry Services, Inc; Linda Chalker-Scott and Eric Eulenberg, WSU Puyallup Research and Extension Center; Peggy Drescher, Charles Shonte, and Glenn Willis, Village of Glen Ellyn; and Kristen Vollrath, The Morton Arboretum.
- © 2012, International Society of Arboriculture. All rights reserved.