Laserfiche WebLink
<br />Woodland protection/percent tree cover. <br />Another technique for delineating which <br />resources to protect focuses less on individ- <br />ual trees and more on entire stands or wood- <br />lands. While only a few ordinances written <br />prior to 1990 took this approach, it has <br />become the method of ch'oice in many juris- <br />dictions with comprehensive tree protection <br />programs and often is combined with protec- <br />tions for specimen trees. There are various <br />ways of implementing a percent cover require- <br /> <br />may be counted toward buffer yard landscap, <br />ing requirements. <br />Speeal area and habitat protection_ A <br />growing number of communities are focusing <br />- their tree and vegetation protection activities on <br />what might be called "special areas": lands with <br />important aesthetic or environmental values that <br />warrant special protection. One of the advan- <br />tages of this approach is that it is usually easier <br />to gamer political support for strong protection <br />.. measures in areas with unique qualities. <br /> <br /> <br />ment. Lake County, Illinois, requires that a flat <br />70 percent of mature woodlands and 50 per- <br />cent of young woodlands on a site be pro- <br />tected as open space. Other jurisdictions <br />have adopted a more flexible approach with a <br />sliding scale that takes into consideration the <br />proposed type of development (e.g., residen- <br />tial vs. industrial) and the amount of existing <br />tree cover on a site (where the amount of tree <br />save area is inversely proportional to the <br />amount of site under tree canopy). <br />Many communities incorporate such <br />techniques into comprehensive protection <br />schemes. For instance, a system could be <br />developed in which a minimum percentage of <br />trees and natural vegetation is preserved, <br />subject to the sliding scale requirements, and <br />supplemented by a requirement that all sig- <br />nificant trees over a certain size be preserved. <br />Distance/buffer requirements. Another <br />common technique used in determining what <br />to protect involves establishing distance or <br />buffer requirements. For example, some com- <br />munities adopt regulations requiring a buffer <br />zone (e.g., 100 feet) between major roadways <br />and any buildings on adjacent private prop- <br />erty. Within the buffer ail trees and vegetation <br />must be retained, with certain limited excep- <br />tions. Existing trees and vegetation retained <br /> <br />102 <br /> <br />Natural areas such as rivers and coastal <br />zones are targeted for protection in some commu- <br />nities. In Fulton County, Georgia, the Chatta- <br />hoochee River Corridor Tributary Protection Act <br />requires active tree protection in an area "exten- <br />ding outward 35 'horizontal feet from the tops of <br />the banks on both sides of all flowing tributaries <br />of the Chattahoochee River." Disturbed areas <br />within the buffer must be replanted to county <br />standards using indigenous riparian vegetation. In <br />Sanibel, Rorida, native vegetation that contributes <br />to beach stability cannot be removed seaward of a <br />coastal construction control line. Strict controls <br />also are placed on vegetation trimming and stump <br />removal. Where undesirable, nonnative species <br />such as Australian pine are removed a revegeta. <br />tion plan must be submitted to reduce soil move- <br />ment caused by wind or water. <br />Many states regulate tree preservation <br />by protecting the habitat of endangered <br />species. Numerous cases have come out of <br />the Pacific Northwest in recent years regarding <br />timberland preserved as spotted owl and <br />eagle nesting sites. Habitat protection is one <br />of the most compelling reasons to save trees, <br />especially where the habitat of an endangered <br />species is at issue. <br />Replacement/mitigation standards. <br />Another increasingly common feature of local <br /> <br />tree preservation laws are provisions requir- <br />ing on-site replacement of trees removed <br />during development or other mitigation <br />measures such as off-site planting or cash- <br />in-lieu contributions. Most such require- <br />ments are based on very specific numerical <br />standards governing the number of trees to <br />be replaced. Fulton County offers specific <br />guidance regarding replacement and mitiga- <br />tion. The quantity of replacement trees must <br />be sufficient to produce a total "site.tree <br />density factor" of no less than 20 units per <br />acre pursuant to administrative guidelines. <br />Detailed standards are provided for trans- <br />planting and selecting quality replacement <br />stock. Specimen trees must be replaced by <br />species with potentials for comparable size <br />and quality. <br />To the extent that these replanting <br />requirements bear some reasonable relation- <br />ship to the number of trees removed (for - <br />example, smaHer replacement trees, some of <br />which may die, may be required in greater <br />numbers to compensate for removal of larger <br />trees), they should withstand challenge. <br />However, planners should be careful not to be <br />overly vague about the size and location of the <br />replacement trees. From a practical stand- <br />point, each community should carefully con. <br />sider what constitutes a rational replacement <br />standard in light of the species involved, spec- <br />imen size, local survival rate of smaller stock, <br />time required for trees to grow to maturity, and <br />similar considerations. This may vary markedly <br />depending on the region of the country. <br />Construction protection measures. Most <br />sophisticated local governments have come <br />to realize that designating trees for protec- <br />tion by strong standards is only half the bat. <br />tie. The best standards being implemented <br />by the most sympathetic developer can be <br />undermined in an afternoon of careless con- <br />struction activities on a site. Bulldozing near <br />a large tree's roots, digging utility trenches, <br />or dumping construction waste close to a <br />tree can' result in the de facto removal of a <br />tree that was designated for preservation. <br />The death may be slower, but it can be just <br />as sure. For example, a few years ago, it was <br />a commonly accepted practice to protect a <br />tree by forbidding any construction activities <br />or excavation'within its so-called dripline (a <br />vertical line extending from the outermost <br />edge of the tree canopy to the ground). <br />Today, the latest thinking is that this old <br />standard may not be sufficient given the fact <br />that most trees do not have a single large <br />tap root, but rather a large network of <br /> <br />ZONING PRACTICE 7.06 <br />AMERICAN PLANNING ASSOCIATION I page 6 <br />