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Originally, Wetland I on the site was given a protection classification of Preserve by the <br />Minnehaha Creek Watershed District (MCWD) inventory. In January 2013 KES completed a <br />MNRAM functional analysis for Wetland 1. Based on the analysis results, a revised protection <br />classification of Manage 2 was determined. MCWD approved the management classification <br />change on January 17 , 2013 (Appendix D). <br />Minnehaha Creek Water District (MCWD) revised their Wetland Protection Rule in September <br />2010. Similar to City of Orono rules, buffers widths are based on the management class of the <br />wetland as determined by a functional analysis. However, MCWD base buffer widths are <br />generally wider than City designated widths. The more restrictive of the widths must be <br />represented on the grading plan. <br />Wetland Buffer Protection, Augmentation, and Enhancement -Existing wetland buffers on <br />the site have a continuous dense layer of perennial grasses that have been unbroken for at least I 0 <br />consecutive years. Buffer adjacent to Wetland 1 will not be disturbed by construction activities; <br />therefore, no buffer augmentation or enhancement is needed. <br />Ecological Management Category Review -The site was assessed for City of Orono Ecological <br />Management Category (EMC) ratings (City Code Sec. 78-1635(9)( 4)), and Figure 6 illustrates <br />observed category areas. Level I EMC areas are associated with wetlands and their buffers. <br />Level 3 E M C areas are suitable for stormwater manage ment. No Level 2 E MC areas (ecological <br />opportunity areas) were observed on the s ite. <br />Invasive Species and Diseased Tree Removal Plan <br />Invasive Species Removal and Management Plan -Areas with invas ive species observed on the <br />site are illustrated in Figure 7. The primary invasive s pecies identified on the s ite was common <br />buckthorn. A detailed common buckthorn management plan is included in Appendix E. Trace <br />amounts of other non-native, invas ive species were observed (common mullein, motherwot1 , <br />garlic mustard). <br />Future seeding of inva s ive s pecies management areas (outside of the graded home lots) is not <br />anticipated because cut stump treatment and foliar spray ing of buckthorn and other trace invas ive <br />s pecies should not result in bare soil or un-vegetated areas. As invas ive species comprise le ss <br />a nd le ss cover over time, native species are 'released'. Native species that have been dormant <br />under the canopy of invas ives are expected to naturall y come back on their own. <br />Although not preci se ly measured , buckthorn trees observed on the s ite represented approximately <br />99% of the total invasive cover. Buckthorn shrubs less than 1.5 inches in diameter will likel y b e <br />foliar treated. Buckthorn trees greater than 1.5 inches in diameter should be stump cut, and their <br />trunks and branches should be chipped or hauled off the s ite. <br />Diseased and Dying Tree Removal Plan -Tree ID number, diameter breast hei g ht (DBH), and <br />species and for all trees tagged during the field tree survey are induced in Appendix C.