Arboriculture & Urban Forestry 34(4): July 2008 Arboriculture & Urban Forestry 2008. 34(4):265–266. 265 Research Note Sixth- and Tenth-Year Growth Measurements for Three Tree Species in a Load-Bearing Stone–Soil Blend Under Pavement and a Tree Lawn in Brooklyn, New York, U.S. Jason Grabosky and Nina Bassuk In 1997, willow oak (Quercus phellos L.), swamp white oak (Quercus bicolor Willd.), and goldenraintree (Koelreuteria paniculata Laxm.) were planted in the right-of-way on Lorimer Street in Brooklyn, New York, U.S. This was one of the earliest commercial installations of the load-bearing stone–soil blends (hereafter called structural soil) developed at Cornell Universi- ty’s Urban Horticulture Institute (Grabosky and Bassuk 1995). The north–south street segment bisects McCarren Park between Driggs Avenue and Bayard Street. Trees were planted as 5.1 to 7.6 cm (2 to 3 in) caliper trees on either side of the street. The west side trees were planted in a continuous trench of structural soil 0.6 m (2 ft) deep by 2.1 m (6.9 ft) wide down the entire block. The structural soil was used as the sidewalk base capped with concrete. Tree openings were 0.9 m by 1.5 m (3 × 5 ft), which were planted after paving and then covered by granite unit block pavers. The east side of the street was a tree lawn planted with the same tree species. The site and the trees have been observed and measured in 1999, 2000, 2003, and 2007. After 3 years, there were no substantial differences in either shoot ex- tension growth or foliage quality between the two sites for the oak species (Grabosky et al. 2002). Goldenraintree was not ana- lyzed or reported in the third year set. This article discusses the trees as observed in Year 6 (2003) and Year 10 (2007). MATERIALS AND METHODS Tree height and trunk diameter at 1.4 m (4.6 ft) were measured on 22 July 2003 and 29 August 2007. Canopy width was mea- sured parallel and perpendicular to the street during the 2007 observation. Comparisons between treatments within obser- vation year used all trees of the species that were in place at the beginning of the study or verified as in place in 1997 to 1998. Imbalance in the number of species replicates on each site (Table 1) required each species to be compared with a nonpara- metric Mann-Whitney confidence interval test on median treat- ment response measures conducted in Minitab 14 (Minitab Inc., State College, PA, U.S.). RESULTS Notes from each observation year were used to construct an estimate of mortality in the paved and tree lawn locations. Of a total of 35 trees in the sidewalk, four total trees were presumed dead over the 10-year period. One Q. phellos was labeled dead and removed in 1999 and replaced in 2000. This replicate was noted as having been planted too deep in 2000 and showed chlorotic, stunted growth in 2000, 2003, and 2007 and was re- moved from analysis. Three other trees in the sidewalk, one other Q. phellos and two K. paniculata, died between 2000 and 2003 and have not been replaced. Overall mortality was four of 35 trees (11%). In the tree lawn, failed trees were replaced and additional trees were established in the site over the first three observations. Planting spaces and replacements were tracked by data sheet site maps and verified with tree tag records when observed on site. The initial 1999 observation measured 26 trees in the tree lawn in a row closest (approximately 2 m [6.3 ft]) to the sidewalk and noted high mortality in willow oak (five of the initial ten were dead). Several blank planting holes (empty mulch circle with disturbed soil) were noted in 1999, 2000, and 2003. Death of some replacements in 2000 prompted mapping and tracking of additional trees (a second row of trees at the other edge of the lawn strip), many of which could be verified as 1998 spring replacement or original 1997 planting. The data analysis used the 17 remaining trees of the original 26 trees measured in 1999 from a total analysis record of 41 trees present in 2007. New plants, replacements, other species, trees in park entrance zones (surrounded by pavement), and verified tenth-year trees without measurements from both 2003 and 2007 have been omitted from this research note. Of the original 26 trees, nine have died, three additional dead/missing trees in the line have been replaced, and two replacement trees have died, suggesting a total of 12 dead from 29 initially planted, or 41% mortality, and two dead from those replaced. For those that survived, there were no significant differences in size between trees planted in the tree lawn or the sidewalk in Years 6 and 10 (Table 1). This is consistent with earlier obser- vations in Year 3 (Grabosky et al. 2002). Increase in trunk diameter in Q. phellos from Year 6 to Year 10 was generally 10 to 13 cm (4 to 5.2 in), comparable to forest conditions (Schlaegel 1990). Similarly, Q. bicolor increases of 6 to 6.5 cm (2.4 to 2.6 in) of trunk diameter growth were comparable to observations in Ohio from high-quality urban and forest lot measures (Quigley 2004). Height increase, as an estimator of shoot growth, on the ©2008 International Society of Arboriculture
July 2008
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