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WETLAND DELINEATION REPORT <br />Silver View Pond Restoration <br />Results <br />October 26, 2023 <br />3.3.1 Wetland 1 <br />Wetland 1 (W01) is a wet meadow community in the western section of the Project. W01 is connected to <br />Wetland 2 (W02) via two culverts on the northwest and southeast ends (Appendix A, Figure 1). <br />Dominant plant species identified at sample points completed within W01 consist of reed canary grass <br />(Phalaris arundinacea, FACW) and Culver's root (Veronicastrum virginicum, FAC). Other common species <br />identified in the wetland are listed on the data forms included in Appendix C. The dominant species within <br />the wetland are comprised mostly of hydrophytic vegetation (OBL, FACW, and/or FAC) and meet the <br />hydrophytic vegetation criterion. <br />The wetland appears to have a seasonally inundated/saturated hydroperiod within the center. No Primary <br />Hydrology Indicators were observed. Secondary indicators of wetland hydrology observed included <br />Geomorphic Position (D2) and a positive FAC-Neutral Test (D5). Therefore, the wetland hydrology criterion <br />was met. <br />Soils within the wetland are mapped by the NRCS as Zimmerman fine sand and Seelyeville muck (Appendix <br />A, Figure 2). The soils observed at the sample points were generally consistent with the Zimmerman series <br />characteristics. Field indicators of hydric soil identified at sample point W01-1w consisted of NRCS field <br />Indicator F6-Sandy Redox surface. Therefore, the hydric soil criterion was satisfied. <br />The wetland boundary was determined based on distinct differences in vegetation, hydrology, soils, and <br />topography consisting of the following: 1) Transition from a wet meadow wetland community dominated by <br />reed canary grass to a mesic woodland upland community dominated by common buckthorn (Rhamnus <br />cathartica, FAC), white oak (Quercus alba, FACU), and black locust (Robinia pseudoacacia, FACU); and <br />2) Transition from an area exhibiting wetland hydrology indicators within the wetland to a lack of wetland <br />hydrology indicators within the adjacent upland; and 3) Transition from soils exhibiting hydric soil indicators <br />to soils lacking indicators of hydric soil conditions. The transition from wetland to upland characteristics <br />generally correlated with a well-defined topographic break. <br />3.3.2 Wetland 2 <br />Wetland 2 (W02) is a shallow open water community that is a part of a wetland complex which is central to <br />all five sections of the Project. W02 is connected to W01 via a culvert on its western boundary. Most of the <br />wetland is made up of the shallow open water community but the sample point was taken in a thin wetland <br />fringe along the open water (Appendix A, Figure 1). <br />Dominant plant species identified at sample points completed within W02 consist of sensitive fern (Onoclea <br />sensibilis, FACW), boxelder (Acer negundo, FAC) and black willow (Salix nigra, OBL). Other common <br />species identified in the wetland are listed on the data forms included in Appendix C. The dominant species <br />within the wetland are comprised mostly of hydrophytic vegetation (OBL, FACW, and/or FAC) and meet the <br />hydrophytic vegetation criterion. <br />The wetland appears to have a seasonally inundated/saturated hydroperiod within the center. No Primary <br />Hydrology Indicators were observed. Secondary indicators of wetland hydrology observed included D2 and <br />D5. Therefore, the wetland hydrology criterion was met. <br />Soils within the wetland are mapped by the NRCS as Seelyeville muck (Appendix A, Figure 2). The soils <br />observed at the sample points were generally consistent with the Zimmerman series characteristics located <br />adjacent to the soil unit. Field indicators of hydric soil identified at sample point W02-1w consisted of NRCS <br />field Indicator Al 1-Depleted Below Dark Surface. Therefore, the hydric soil criterion was satisfied. <br />