Laserfiche WebLink
, <br /> ' <br /> Wetland boundaries were marked at the site by blaze-orange "wetland boundary" flagging <br /> ' attached to 4-foot wooden lath or pin flags. Where vegetation was dense, to assist in locating the <br /> flagged lath (wetland edge), a second piece of flagging was attached to a nearby tree or shrub <br /> branch. The "wetland boundary" is considered to be the topographically highest extent of the <br /> ' wetland basin; areas below the staked boundary met the three required wetland criteria while <br /> areas above were lacking in one or more of these criteria. <br /> � Wetland classification followed methods described by Cowardin et al. (1979) and used in the <br /> NWI (e.g. PEMB, PSS1C, etc.), completed by the U.S. Fish and Wildlife Service. The Circular <br /> , 39 Classification System (Shaw and Fredine 1956) is also given (e.g., Type 1, Type 2...etc.). <br /> The indicator status of plants, as described in Appendix B, was deternuned using the National <br /> List of Plant Specces That Occur cn Wetlands—Region 3 (Sabine 1999). <br /> ' RESULTS <br /> � Background Information-(Office-Based Investigation) <br /> The USGS Quadrangle map (Figure 1) outlines, in red, the study parcel and its location within <br /> the City of Orono, MN. The approximate wetland boundaries and the boundary of the storm <br /> , water retention pond as illustrated in yellow (Figure 4) were developed, in part, using data <br /> provided by the National Wetlands Inventory Map(Figure 2). <br /> � The Hennepin County Soil Survey Map (Figure 3) indicates the presence of hydric Klossner <br /> Muck Series Soil (blue cross hatching) and nonhydric Le Sueur and Lester Series Soils (red <br /> stippling) within the parcel(Figure 3). A description for these soil types is given in Appendix C. <br /> ' Site Visit <br /> ' SER personnel examined the subject property for those areas meeting jurisdicdonal wetland <br /> criteria. Boundaries were delineated for those wetlands meeting jurisdictional wetland criteria <br /> (Figure 2).The approximate boundary for the parcel is illustrated in red on all figures. Detailed <br /> ' soil, vegetation, and hydrology data for the delineated wetland and adjacent upland are provided <br /> in Appendix A. <br /> ' The wetlands are classified as Type-3 PEMCd Wetlands (Figure 2; U.S. FWS Circular 39 and <br /> Cowardin et al., 1979, respectively). T'he wetland boundary for Wetland 2 was marked with <br /> approximately 48 pieces of wooden lath with blaze orange wetland flagging attached. The <br /> ' boundary for Wetland 1 was marked with approximately 15 pieces of flagged lath. <br /> The storm water retention pond was clearly marked with orange pin-flags labeled 2-1 through 2- <br /> ' 15. Reed Canary Grass is the dominant vegetation with the pond and there are culverts at either <br /> end. The soil was saturated at the surface at the time of the site visit. <br /> � Field evaluation and subsequent chazacterization of soil at the site confirm the presence of hydric <br /> soils at the wetland sample point (Klossner, Figure 3, Appendix C). These data are summarized <br /> within Tables 1-4. The occurrence of dominant wetland vegetation, primary hydrology, and a <br /> , positive FAC-Neutral Test support the presence of two jurisdictional wetlands within the study <br /> Svoboda Ecological Resources 9 2180 Abingdon Way <br /> Project No.2007-056-03 Orono,Minnesota <br /> � <br />