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<br />site that has regenerated with opportunistic plant species. The Minnesota Biological Survey does not show any <br />sites of biodiversity significance or native plant communities within the AUAR study area. <br />Just east side of the AUAR study area is the proposed Rice Creek North Regional Trail. The 2003 Rice Creek <br />North Regional Trail Master Plan Amendment and 2006 Ramsey County System Plan identified 49 acres of <br />TCAAP property to be acquired as a wildlife corridor. According to the 2013 Rice Creek North Regional Trail <br />Master Plan Amendment (approved by the Metropolitan Council on August 28, 2013), an additional 60 acres is <br />proposed to be added to the wildlife corridor (Figure 7-1). This wildlife corridor provides habitat for birds, small <br />mammals, and invertebrates and has several osprey nesting platforms. It is also provides a wildlife habitat <br />connection between the open space of AHATS and the open space of Rice Creek. <br /> <br />b.D-(,) <br />ESCRIBE RARE FEATURES SUCH AS STATELISTED ENDANGERED THREATENED OR SPECIAL CONCERN <br />,,MCBSSB <br />SPECIES NATIVE PLANT COMMUNITIES INNESOTA OUNTY IOLOGICAL URVEY ITES OF IODIVERSITY <br />S,. <br />IGNIFICANCE AND OTHER SENSITIVE ECOLOGICAL RESOURCES ON OR WITHIN CLOSE PROXIMITY TO THE SITE <br />P(LA-____)/(ERDB <br />ROVIDE THE LICENSE AGREEMENT NUMBER ANDOR CORRESPONDENCE NUMBER <br />_20140096)NH <br /> FROM WHICH THE DATA WERE OBTAINED AND ATTACH THE ATURAL ERITAGE LETTER FROM THE <br />DNR.I <br /> NDICATE IF ANY ADDITIONAL HABITAT OR SPECIES SURVEY WORK HAS BEEN CONDUCTED WITHIN THE SITE <br />. <br />AND DESCRIBE THE RESULTS <br />A DNR database search for the AUAR study area and surrounding area identified a number of resources <br />known to occur near the AUAR study area, and general ecological designations portions of the site. There <br />are no state or federal listed threatened or endangered species or rare plant communities recorded within <br />the AUAR study area in the DNR NHIS database. State-listed occurrences found beyond the AUAR study <br />area in or near Marsden Lake on the AHATS property include a known populati <br />(Emydoidea blandingii state-listed threatened species); trumpeter swans (Cygnus buccinator state-listed <br />species of special concern); and a population of the plains pocket mouse (Perognathes flavescens state- <br />listed species of special concern, between the gravel pit and Marsden Lake). <br />for this species includes calm, shallow wetlands (Type 1-3) with mud bottoms and abundant aquatic <br />vegetation (e.g., cattails, water lilies). Nesting occurs in open (grassy or brushy) sandy uplands, often up to <br />a mile from water bodies. The majority of the wetlands within the AUAR study area are not large enough to <br />support turtles (ditches), and most of the soils are disturbed urban land. There is no record of the turtle <br />within the AUAR study area; however, turtles are known to occur within the vicinity, and may occur within <br />the project boundary. A turtle fact sheet that describes the habitat use and life history of the species along <br />with two lists of recommendations for avoiding and minimizing impacts to the turtles are included in <br />Appendix B. <br />Trumpeter swans (Cygnus buccinator), a state-listed species of special concern, have been observed <br />nesting within the AHATS site on Marsden Lake. Nesting habitat includes lakes and ponds with 100 meters <br />of open water for take-off, stable levels of unpolluted water, emergent vegetation and low levels of human <br />disturbance. The AUAR study area does not contain any suitable nesting habitat for trumpeter swans. <br />The plains pocket mouse (Perognathus flavescens), which is a state-listed species of special concern, has <br />also been documented within the AHATS site. There are no known occurrences of the mouse within the <br />AUAR study area; however the northwestern corner of the site was noted by the DNR as potentially <br />containing suitable habitat for the mouse. Suitable habitat is restricted to open, well-drained areas, typically <br />on sandy soils with sparse, grassy or brushy vegetation. The grass vegetation in the northwest corner of the <br />site may be too dense for this species and too far from the gravel pit population to support this species <br />(Birney, 1999). <br /> <br /> <br />July 2014 Final AUAR 18 <br />