1. General. Landscaping plants intercept rainfall, reduce storm water runoff, prevent erosion, and reduce the need for detention. Landscape plants also provide shade and reduce the temperature created by additional impervious surfaces. Plants release moisture back into the environment, improve air quality, and remove contamination from the soil and water by absorbing excess nutrients, filter sediments, and break down pollutants. Planting native plants helps provide habitat, food, and protection for native species and ecosystems. Planting native species generally increases the chance for long term survivability of the plant because they are naturally adapted to local conditions. Planting non-native species and cultivars could be incorporated in designs when they provide a superior plant for spatial constraints and urban stress mitigation found in local site conditions. Existing significant trees which help contribute to the sense of place should be preserved to the maximum extent practical.
2. Design Guidelines.
A. Native plant materials should be incorporated in all designs. The use of native plant material can help improve water quality, provide additional and improved wildlife habitat, and typically adapt to local conditions which then require less maintenance. Native plants must be used near greenways, suburban forested areas, wetlands, and riparian areas.
B. Except as noted above, non-native plants may be included in place of a native plant if it is not considered invasive and the plant does not introduce pests or diseases. A non-native plant may be incorporated into designs when they prove to be better suited for the soil, environment, or spatial constraints, urban stress mitigation, and integration into the surrounding ecosystem.
C. The following is a list of invasive plants which may not be used in any urban planting schedule:
(1) Trees. Tree-of-heaven (ailanthus altissima), norway maple (*acer platanoides), sycamore maple (acer pseudoplatanus), empress tree (paulownia tomentosa), callery pear (*pyrus calleryana), siberian elm (ulmus pumila)
(2) Shrubs. Japanese barberry (*berberis thunbergii), European barberry (berberis vulgaris, russian olive (elaegnus angustifolia), autumn olive (elaeagnus umbellate), winged euonymus (*euonymus alatus), border privet (ligustrum obtusifolium), common privet (ligustrum vulgare), tartarian honeysuckle (lonicera tartarica), standish honeysuckle (lonicera standishii), morrow’s honeysuckle (lonicera morrowii), Amur honeysuckle (lonicera maackii), bell’s honeysuckle (lonicera morrowii x tatarica), common buckthorn (rhamnus catharticus), glossy buckthorn (rhamnus frangula), wineberry (rubus phoenicolasius), multiflora rose (rosa multiflora), Japanese spiraea (*spiraea japonica), guelder rose (*viburnum opulus var. opulus).
(3) Grasses. Cheatgrass (bromus tectorum), Japanese stilt grass common reed (phragmites australis), reed canary grass (phalaris arundinacea), johnson grass (sorghum halepense), and bamboo (poaceae), shattercane (sorghum bicolor ssp. drummondii)
(4) Flowers. Garlic mustard (alliaria petiolata), goutweed aegopodium podagraria), bull thistle (crisium vulgare), canada thistle (cirsium arvense), musk thistle (carduus nutans), jimsonweed (datura stramonium), goatsrue (galega officinalis), giant hogweed (heracleum mantegazzianum, dame’s rocket (hesperis matronalis), purple loosestrife (lythrum salicaria, L. virgatum), eurasian water-milfoil (myriophyllum spicatum), star-of-bethlehem (ornithogallum nutans, umbellatum), japanese knotweed (polygonum (falopia) cuspidatum/ polgonum sachalinense), wild parsnip (pastinaca sativa), beefsteak plant (perilla frutescens), lesser celandine (ranunculus ficaria), water chestnut (trapa natans).
(5) Vines. Fiveleaf akebia (akebia quinata), porcelain-berry (ampelopsis brevipedunculata), oriental bittersweet (celastrus orbiculatus), japanese honeysuckle (lonicera japonica), kudzu (pueraria lobata), mile-a-minute vine (polygonum perfoliatum).
* Species with cultivars that are known to be non-invasive may be acceptable within a planting plan.
3. Street Trees / Screening / Vegetative Buffering.
A. Any existing vegetation that is in appropriate locations, of an acceptable species and quality may be used to fulfill landscaping or buffering requirements.
B. Any landscaping should create, or be part of the process to create larger landscape patches and corridor ecosystems and larger interior areas and less edge areas. Connectivity to existing landscaping shall be encouraged.
C. In order to aid surveillance and minimize the potential for crime, planting shall also be sited, massed, and scaled to maintain visibility of doors and first floor windows from the street and from within the development to the greatest extent possible. Planting patterns shall not obstruct sight lines or create isolated areas, especially near pedestrian walking paths.
D. Trash disposal areas, such as dumpster or compactor sites, shall be effectively screened so as to be screened with a combination of architectural masonry (or fencing) and/or landscaping with a height of at least 6 feet.
E. Open areas should also include but not be limited to at least 4 of the following:
(1) Seasonal planting areas;
(2) Large deciduous trees;
(3) Seating;
(4) Pedestrian scale lighting;
(5) Gazebos or other decorative shelters;
(6) Play structures for children;
(7) Natural environment areas;
(8) Recreational amenities; or
(9) Trails.
F. All planting shall be performed in conformance with good nursery and landscape practice. Plant materials shall conform to the standards recommended by the American Association of Nurserymen, Inc., in the American Standard of Nursery Stock, ANZIZ60, current edition, as amended.
(1) Provide a landscape plan note indicating that the top of the main order root (first large set of roots that divide from the trunk) shall be planted no lower than 1 or 2 inches into the soil.
(2) Planting designs are encouraged to share planting space for optimal root growth whenever possible. Continuous planting areas vs. isolated planting boxes are encouraged.
(3) No staking and wiring of trees shall be allowed without a maintenance note for the staking and wiring to be removed within 1 year of planting.
(4) All street trees shall be provided by the applicant in accordance with the following standards:
(a) The trees shall be nursery grown in a climate similar to that of the locality of the project. Varieties of trees within the right-of-way shall be subject to the approval of the authority that accepts ownership of the street.
(b) All trees shall have a normal habit of growth and shall be sound, healthy, and vigorous; they shall be free from disease, insects, insect eggs, and larvae.
(c) The trunk caliper, measured at a height of 6 inches above finish grade shall be a minimum of 3 inches.
(d) Tree planting depth shall bear the same relationship to the finished grade as the top of the root ball or original grade of origin.
(e) All required landscape plants shall be maintained and guaranteed for a length of 24 months from the date of planting. No more than 1/3 of the tree or shrub shall be damaged or dead without replacement. Replacement plants shall conform to all requirements of this section and shall be maintained after replanting for an additional 24 months.
(f) The plant’s growth shall not interfere with the street cartway, sidewalk, signage, easements, clear sight triangles, or utility line. Within the clear sight triangle, typical branching shall not be within 10 feet of ground level after 10 years of growth.
(g) No one species shall comprise more than 33% of the entire number of street trees in a particular development.
(h) Existing significant trees and natural features, such as drainage corridors, shall be preserved to the maximum extent practicable and incorporated into site plans and site design as major amenities.
(i) If a significant tree is designated to be preserved but is removed or substantially damaged during the clearing, grading, or construction, the applicant or developer shall be required to replace the removed or damaged tree with one approved by the Shade Tree Commission.
G. Street trees shall be provided in all land developments which include new streets.
(1) Street trees shall not be located farther than 40 feet away from the new street right-of-way.
(2) The number of street trees shall be based on 2 street trees required for every 100 linear foot of new street measured from the centerline.
(3) The spacing of trees shall be based on the size of the tree canopy at maturity with trees spaced no closer than 30 feet on center if the tree canopy is less than 30 foot spread at maturity, spaced 30-60 feet on center if the tree canopy is 30 to 50 feet spread at maturity, and street trees spaced 50 to 100 feet on center if the tree canopy is over 50 feet spread at maturity. When a less formal arrangement is desired, where more massing is appropriate, or improvements such as benches are located grouping of street trees is encouraged.
(4) Street trees shall be one of the following species:
Common Name | Botanical Name | Height/ Spread | Drought Tolerances
|
Soil Type
|
Soil Acidity/ Aerosol Salt Tolerance
|
Soil Saturation Preference
|
Root Pattern
|
Canopy Structure/ Growth Rate
|
Common Name | Botanical Name | Height/ Spread | Drought Tolerances
|
Soil Type
|
Soil Acidity/ Aerosol Salt Tolerance
|
Soil Saturation Preference
|
Root Pattern
|
Canopy Structure/ Growth Rate
|
Red Maple | Acer rubrum | 75/35 | Moderate | Clay; loam; | Acidic/ Low tolerance | Extended flooding to well drained | Large surface roots | Upright oval canopy/ fast growing |
Sugar Maple | Acer saccharum | 70/40 | Sensitive to reflected heat and drought | Sand; loam. Not compacted | Acidic; alkaline/Not tolerant | Well drained | Often shallow | Dense Oval/ Mod-slow growing |
River birch | Betula nigra | 40-50/ 25-35 | Moderate | Clay; loam | Acidic | Extended flooding to well drained | Not a problem | Narrow- pyramidal crown/ Fast growing when moist |
Common Hackberry | Celtis occidentalis | 45-80/ 40-50 | Highly tolerant | Clay; loam | Tolerant of highly alkaline to moderate acidic | Extended flooding to well drained | Large surface roots | Round/ Prune to prevent weak branch crotches |
American Yellowwood | Cladrastis kentuckea | 30-50/ 40-50 | Moderate | Clay; sand; loam | Alkaline; acidic | Occasional wet to well-drained | Surface roots when wet | Round/ Moderate/ Prune structure |
American beech | Fagus grandifolia | 50-75/ 40-60 | Moderate to low | Sand; loam | Acidic/ Low Tolerance | Needs well-drained | Surface roots/ Needs space | Very dense oval/ Moderate |
White ash | Fraxinus americana | 50-80/ 40-60 | Moderate | Sand; loam | Alkaline; acidic/Highly tolerant | Extended flooding to well- drained | Large surface roots/ Needs space | Oval/Fast growing |
Green Ash | Fraxinus pennsylvan- ica | 60-70/ 45-50 | Highly tolerant | Sand; loam; clay | Alkaline; acidic/ Moderately tolerant | Extended flooding to well- drained | Large surface roots develop when confined | Upright/ Fast; Prune structure to develop trunk |
Thornless Honey-locust | Gleditsia triacanthosinermis | 50-70/ 35-50 | Highly tolerant | Clay; sand; loam | Alkaline; acidic/Highly tolerant | Occasional wet to well- drained | Can grow surface roots | Open oblong |
Sweetgum | Liquidambar styraciflua | 60-75/ 35-50 | Moderate to little | Clay; sand; loam | Acidic/ Moderately tolerant | Extended flooding to well- drained | Surface roots when moist | Pyramidal/ Extreme sensitivity to construction |
Tuliptree | Liriodendron tulipifera | 80-100/ 30-50 | Moderate | Sand; loam | Acidic/ No tolerance | Well- drained to occasional wet | Not a problem Needs space | Oval/ Moderate growth |
Blackgum/ Sourgum | Nyssa sylvatica | 65-75/ 25-35 | Highly tolerant | Clay; loam | Acidic/ Moderately tolerant | Extended flooding to well- drained | Not a problem; deep roots | Pyramidal/ Slow growth |
American Hophorn- beam | Ostrya virginiana | 25-50 | Tolerant once establish | Sand; loam | Poor salt tolerance pH adaptable | Prefers moist when young | Not a problem | Rounded |
Sycamore | Platanus occidentalis | 75-90/ 50-70 | Highly tolerant | Clay; loam; should not dry out | Alkaline; acidic/ Moderately tolerant | Extended flooding to well- drained | Can grow surface roots | Dense pyramidal/ Fast growing |
White Oak | Quercus alba | 60-100/ 60-80 | Moderate to low | Sand; loam; should not dry out | Acidic/ Highly tolerant | Occasional wet to well- drained | Not a problem | Pyramidal/ Slow growing |
Shingle Oak | Quercus imbricaria | 40-60/ 40-60 | Tolerant intermittent drought | Rich; deep; well drained | Alkaline soils up to 7.5 pH | Moist | Not a problem | Rounded/ Transplants well |
Chestnut Oak | Quercus montana | 50-60/ 40-60 | Highly tolerant | Sand; loam | Acidic/ unknown salt tolerance | Well- drained | Root flare when older | Round/ Moderate growth |
Red Oak | Quercus rubra | 60-70/ 50-60 | Highly tolerant | Sand; loam | Acidic/ Highly tolerant | Well-drained | Can for large surface roots | Dense; round/Fast growth; Train into one leader |
Swamp White Oak | Quercus bicolor | 50-70/ 50-70 | Moderate | Clay; sand; loam | Acidic/ Moderate tolerance | Extended flooding to well- drained | Not a problem | Round/ Moderate growth; long lived |
Basswood/ American Linden | Tilia americana | 50-80/ 35-50 | Moderate | Sand; loam | Acidic; alkaline/ Low tolerance | Well- drained | Not a problem; Needs space | Dense; Pyramidal/ Moderate |
Other tree species may be used provided acceptable information is submitted to indicate that the species are hardy trees or fits the sites ecosystem. | ||||||||
4. Ground Cover. Ground cover shall be provided on all areas of the project to prevent soil erosion. All areas which are not covered by paving, stone, or other solid material shall be protected with a suitable ground cover, consisting of spreading plants including sods and grasses less than 18 inches in height.
5. Existing Wooded Areas. No more than 20% of existing woodlands located in environmentally sensitive areas shall be destroyed or altered. If the applicant can prove that invasive species are within either of these areas, then the percent of woodlands to be removed may be increased to eradicate invasive species.
6. Tree Protection Zone.
A. Prior to construction the tree protection zone shall be delineated at the dripline of the tree canopy. All trees scheduled to remain shall be marked; however, where groups of trees exist, only the trees on the edge need to be marked. A 48-inch high snow fence or 48-inch high construction fence mounted on steel posts located 8 feet on center shall be placed along the boundary of the tree protection zone.
B. No construction, storage of material, temporary parking, pollution of soil, or regrading shall occur within the tree protection zone. When there is a group of trees, the tree protection zone shall be based on the location of the outer trees.
(Ord. 614, 5/11/2015)