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Restaurant Row (p. 47) <br />"To maximize the ecological functionality and human experiential values of the habitat <br />zone from "restaurant row' toward the river, we recommend that that master <br />plan... integrate what are currently shown as distinct zones for the pollinator prairie, <br />upper /midbank zone and riparian floodplain zone into a more or less continuous plant <br />community gradient. " <br />Species selection and infrastructure design for different habitat zones (p. 48) <br />"LEED certification has been identified as a potential goal for the master plan. The term <br />"native or adaptive species " comes from the LEED ND landscaping criteria, which <br />reference a criteria for new landscaping of 80 -90% "native or adaptive species. " <br />Although LEED defines such a species as "low maintenance but not invasive ", the term <br />"adaptive" species has no any accepted or standardized ecological meaning and we <br />strongly recommend it not be used in the master plan. Because ecological functions are <br />a key dimension of the EWEB design, it is essential to use terms with precise meaning. <br />For instance, a non - native species that is well adapted to the climate and soils so that it <br />needs little care, management or supplemental water, fertilization etc. could be relatively <br />benign, or it could be a major invasive exotic species. Our recommendation is that only <br />natives be used in the upper /midbank habitat zone so as to maintain high ecological <br />value, and that plant species for the urban habitat zone be specified as "natives and non- <br />invasive introduced species that require minimal supplemental water, fertilization or pest <br />or disease control", rather than "adaptive plant species. " <br />Ecological Functions, Habitat Quantity and Habitat Quality <br />Master plans are intended to guide future design and planning implementation but do not <br />necessarily specify the outcomes in a sufficiently detailed or "hard and fast" manner to support a <br />quantitative assessment of ecological functions. In this final section of the full report we <br />described five qualities that could provide a qualitative baseline for assessment: ecological <br />function type, habitat size, habitat quality, habitat connectivity, and management of ecological <br />dynamism. Such an assessment would provide a foundation for understanding the potential <br />consequences of altering or further specifying different aspects of the master plan when the <br />project shifts from the planning phase to the design phase. We refer the reader to this section of <br />the full report for further detail. <br />For ecological performance to be assessed post - occupancy, there are a number of mechanisms <br />that can be used ranging from assessments of native species diversity and native v. exotic species <br />cover, to more integrative measures of the success of indicators species such as those listed in <br />Appendix B of the full report. One issue not addressed in the original report that will become <br />central in the design phase is the thoughtful quantitative specification of appropriate ranges of <br />native versus exotic plant species diversity and cover in different zones of the site. For example, <br />specifying the number of native versus exotic species is useful but says nothing about their <br />relative abundances. Specifying the number of individual plants of each type introduced at the <br />time of planting is also useful but doesn't address the total amount of area covered by each type <br />since different plant species grow to different sizes. Specifying the relative area covered by each <br />type of plant is perhaps the most useful measurement. Furthermore, specifying plant <br />26 <br />