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consumption and environmental impact. Ac- <br />cording to the EPA, the typical suburban lawn <br />consumes 10,000 gallons of water a year above <br />and beyond rainwater, creates grass clippings <br />that consume 25 to 40 percent of landfill space <br />during the growing season, and requires the <br />use of lawnmowers with gas -powered engines <br />that emit more hydrocarbons than a typical car <br />(National Wildlife Federation n.d.). <br />How can a community address this is- <br />sue? Establish turf grass limits, and create <br />landscaping standards that rely on the use <br />of native and, where appropriate, drought - <br />tolerant species. There are multiple examples <br />of zoning codes across the country that either <br />recommend limitations or establish specific <br />restrictions on the amount of turf grass used <br />to a relatively small percentage of the site, <br />as well as communities that have sponsored <br />turf grass buy-back programs. As an example, <br />Rio Rancho, New Mexico, regulates turf grass <br />to cover no more than 1,00o square feet or <br />20 percent of the total lot area, whichever is <br />less, while also prohibiting home owner as- <br />sociations bylaws from requiring a minimum <br />amount of grass (§154.o5.G). <br />Avoiding watering issues altogether, <br />some communities also permit the use of <br />artificial turf, such as Simi Valley, California, <br />which permits up to 75 percent of the land- <br />scape area to be covered with artificial turf <br />(§933.03o). <br />Native and drought -tolerant plant materi- <br />als along with non -plant groundcovers are <br />both excellent primary plant sources in local <br />landscapes and best choice substitutes for <br />the use of turf grass. What is "native" is sub- <br />ject to some scholarly discussion; however, <br />most of the discussion circles around the <br />idea that native plants "occur naturally in a <br />particular region, state, ecosystem, and habi- <br />tat without direct or indirect human actions" <br />(Morse et al. 1999). Native plants have, over <br />time, adapted to local soil and climate condi- <br />tions, which means that they generally need <br />less watering and fertilizing than non-native <br />plants do. State and regional native plant lists <br />are available online and are also typically <br />available through state university agricultural <br />and landscaping programs. <br />Plants that may be able to survive in <br />long-term drought conditions have differ- <br />ent, and sometimes confusing, names. Xeric <br />plants function normally in dry conditions. <br />Drought -tolerant and drought -resistant plants <br />use survival mechanisms, such as temporarily <br />defoliating or going dormant, to survive dry <br />conditions, but these plants still may die in <br />prolonged drought situations (Silver 2015). <br />"Native" and "drought -tolerant" are not in- <br />terchangeable terms. Some native plants are <br />xeric or drought tolerant; others are not. When <br />drafting zoning standards, it is important to <br />be specific about the category of plant the <br />community wants to promote or require. This <br />is best accomplished through good defini- <br />tions, such as Sanford, Florida's definition of <br />drought -tolerant: "native, non-invasive plants <br />which will survive and flourish with compara- <br />tively little supplemental irrigation," (Part <br />III, Schedule J, §6.o) and this definition of <br />xeriscaping from the University of Florida IFAS <br />Extension: "landscaping with slow-growing, <br />drought -tolerant plants to conserve water and <br />establish a waste -efficient landscape" (2006). <br />Within a zoning context, requirements <br />for the preservation and planting of native and <br />drought -tolerant plants can range from very <br />general to very specific. Scottsdale, Arizona, <br />starts by identifying native plants already on <br />ments must achieve a minimum number of <br />points based on the size of the site through a <br />combination of plants chosen from the menu <br />(§25-16.7). The city establishes a preference <br />for the use of native Missourian plants in the <br />intent section of the regulations as follows: <br />"[p]romote the use of Missouri native plants <br />that are more adaptable to the local climate <br />extremes, are drought tolerant, low mainte- <br />nance, and thus provide a sustainable, eco- <br />logically balanced environment" (§25-16.2.H). <br />The regulations then support this intent by <br />allocating more points to the use of native <br />plants. For example, Missouri native canopy <br />trees are worth two points per tree, while <br />other canopy trees are worth 1.5 points. <br />The Miami -Dade County, Florida, Land- <br />scape Code establishes the basic objective <br />"to use xeriscape (Florida Friendly) principles <br />to reduce water consumption, to expand the <br />use of native species and to protect existing <br />native habitats, to promote energy conserva- <br />tion through the use of landscape and the use <br />of landscape design as an integral part of the <br />site and architectural design of our commu- <br />nity" 618A -2(A)). The code establishes: (1) a <br />maximum lawn area as a percent of net lot <br />area—residential uses are permitted <br />about 5o to 6o per cent lawn area— <br />planted in "species well adopted <br />to localized growing conditions <br />in Miami -Dade County" (§18A - <br />6(A)(1)); (2) a minimum num- <br />ber of trees to be planted—"of <br />a species normally grown in <br />Miami -Dade County"—and 8o <br />per cent of which are listed <br />in the Miami -Dade Landscape <br />Manual (§18A -6(C)(12)); and <br />(3) a shrub mix that includes at <br />least 3o per cent native species, <br />5o per cent low maintenance and <br />drought tolerant, and 8o per cent listed <br />in the Miami -Dade Landscape Manual, the <br />Miami -Dade Street Tree Master Plan, or the <br />University of Florida's list of Low -Maintenance <br />Landscape Plants for South Florida (§18A -6(D) <br />(1)). The landscape plan review process con- <br />siders the preservation of native vegetation, <br />planting in hydrozones, use of native plant <br />species, and reestablishment of native habi- <br />tats (§18A-7). <br />Finally, when considering water conser- <br />vation in landscaping standards, communities <br />should also review any irrigation standards <br />in the zoning code. The type and design of <br />Q <br />agefrr edbud is co` <br />-sMi4ourir n ® Is;give p e ere <br />a us bytheMa land ' eig <br />andsca a e;design s an, ards <br />the site through the creation of a site-specific <br />"native plant program" prior to construction <br />(§§46 -1o5 -12o). Certain native plants, such <br />as slow-growing desert trees and cacti, are <br />protected, and the city uses the native plant <br />program to work with the applicant to deter- <br />mine how best to work around or relocate <br />these plants. <br />Maryland Heights, Missouri, uses a <br />menu and point system for plant selection in <br />its landscape design standards; all develop- <br />ZONINGPRACTICE 9.15 <br />AMERICAN PLANNING ASSOCIATION I page 5 <br />