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monitoring of reproduction and cub survival, 2) additional (improved) measurements of body condition, heart function, and wound healing, 3) examination of habitat use and movements with GPS telemetry, 4) investigation of female dispersal near the southern fringe of the expanding bear range (Garshelis et al. 2004), and 5) monitoring the incidence of nuisance bears and in particular any conflicts with soldiers and military training. In 2008, the MNDNR Forest Wildlife Populations and Research Group initiated a study site at the edge of bear range in northwestern Minnesota. The goal is to assess the factors that may limit range expansion, including highly fragmented forested habitat, lack of agricultural crops that bears can eat, and human-related mortality. Comparisons will be made between GPS collared bears at the northwestern edge of bear range and collared bears at Camp Ripley, along the southern edge of their range (Garshelis et al. 2007). Mortalities and Reproduction Ground and aerial tracking were used to monitor reproductive success, movements and survival of ten collared black bears (eight females, two males) through 2009 (Table 12). Bear #2063 had one cub in 2005 and 2007; this year (2009) at eight years old, she had three cubs and continues to occupy the northeast portion of Camp Ripley. Bear #2610 was an orphaned cub placed with bear #2063 in March 2007. Two years old in January 2009, she spent most of the year on Camp, but occasionally moved across the Crow Wing River. In mid-November she was on Camp, but crossed the Crow Wing River again and denned in a less populated area of southwest Baxter, Minnesota (Figure 43). Bear #2079 (seven years old in 2009) had three cubs in 2007 and an orphan cub was also placed with her that spring. All four cubs, including the orphaned cub, survived to den in December, 2007. Three of the four, including the orphan, were females; in March 2008 all three females were collared with expandable collars and survived through the summer, however, the orphan (#2611) has not been located since August 2008. The other two females (#2107 and #2108) were not handled at den visits in 2009, but were located throughout the year in #2079‟s home range. Bear #2092 (four years old Jan. 2009) had two cubs in 2009, she is one of bear #2079‟s cubs and her territory overlaps her mother‟s. In the fall of 2008 a landowner reported that he had found a bear den on his land south west of Green Prairie Fish Lake. On March 12, 2009 a 200 pound male bear (#2122) was collared at the site. This bear occupied much of #2079‟s territory and was on Camp several times during the year. Although bear #2079 can still be found on Camp occasionally, she is usually located south of Camp (Figure 44). 2009 Conservation Program Report Page 66
Figure 43. Locations for black bear #2063 and #2610 at Camp Ripley, 2009. Page 67 2009 Conservation Program Report
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This document is made available ele
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Camp Ripley and Arden Hills Minneso
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TABLE OF CONTENTS TABLE OF CONTENTS
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Program Overview ..................
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EXECUTIVE SUMMARY This Conservation
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In 2009, the environmental team gav
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Figure 1. Location of Camp Ripley a
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land use activities between militar
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all of the buildings on AHATS have
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Figure 3. Forest stands re-inventor
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Figure 4. Forest Inventory and Anal
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Figure 5. Location of timber sales
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Table 4. Timber sale summary at Cam
Page 32 and 33: 2009 Sales Hodgden Logging B011023
Page 34 and 35: Specific information regarding thes
Page 36 and 37: Figure 10. VEGETATION MANAGEMENT Ca
Page 38 and 39: Figure 11. Fire units burned for ec
Page 40 and 41: Camp Ripley and Arden Hills Army Tr
Page 42 and 43: Figure 14. Picture of the large sca
Page 44 and 45: Figure 17. Results from spraying a
Page 46 and 47: techniques, to current 2009 updates
Page 48 and 49: Figure 20. Total phosphorus results
Page 50 and 51: Totals and Trends Camp Ripley provi
Page 52 and 53: The ovenbird, one of the most commo
Page 54 and 55: methodology were also considered, h
Page 56 and 57: shrubland/grassland sparrow was hig
Page 58 and 59: Woods (3 single boxes) and Camp Rip
Page 60 and 61: Figure 26. Wood duck nesting box lo
Page 62 and 63: Figure 28. Bald eagle nests at and
Page 64 and 65: Figure 29. Owl survey route at Camp
Page 66 and 67: Red-shouldered Hawk (Buteo lineatus
Page 68 and 69: Figure 33. Red-shouldered hawk call
Page 70 and 71: Ruffed Grouse (Bonasa umbellus) Ruf
Page 72 and 73: Figure 37. Ruffed grouse drumming s
Page 74 and 75: (Helianthus spp.), and grass (Poa s
Page 76 and 77: Table 11. Gray wolves captured at C
Page 78 and 79: Figure 40. Locations for Wolf #31 a
Page 80 and 81: Wolf Mortalities Wolf #28 was first
Page 84 and 85: Figure 44. Bear #2079‟s (7 year o
Page 86 and 87: Figure 45. Bear #2081‟s home rang
Page 88 and 89: Scent Post Survey The MNDNR has con
Page 90 and 91: Cougar (Puma concolor) and Canada L
Page 92 and 93: Figure 50. Cougar and Canada lynx d
Page 94 and 95: Ground and aerial tracking were use
Page 96 and 97: Figure 51. Calculated 90% minimum c
Page 98 and 99: Many problem areas can be addressed
Page 100 and 101: Figure 54. Locations of ANABAT surv
Page 102 and 103: Table 16. Summary of Blanding‟s t
Page 104 and 105: Figure 56. Observations and nest lo
Page 106 and 107: Figure 59. Precipitation (inches) a
Page 108 and 109: Figure 62. Anuran survey routes at
Page 110 and 111: Table 17. Anuran survey index data
Page 112 and 113: Grassland plots (n=7) contained 20
Page 114 and 115: Average Number of Species per Plot
Page 116 and 117: Henslow’s sparrow (Ammodramus hen
Page 118 and 119: large (See Hunting Programs section
Page 120 and 121: Table 22. Small mammal live trappin
Page 122 and 123: and was completed by 3:30 PM. Surve
Page 124 and 125: Table 24. Bird species observed at
Page 126 and 127: Lake Allot is managed for a wide di
Page 128 and 129: Complete details regarding the ACUB
Page 130 and 131: Figure 72. Camp Ripley ACUB fiscal
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Range and Training Land Assessment
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Figure 73. Farmstead mitigation sit
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A natural resource damage assessmen
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UTILIZATION Derived Digital Terrain
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HUNTING PROGRAMS Camp Ripley has ha
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Table 32. Deployed soldier‟s arch
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Table 34. General public archery wh
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AHATS Volunteer Archery Deer Hunt T
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2009 Conservation Program Report RE
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Koper, N. and R. J. Brooks. 2000. E
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U.S. Department of Agriculture. 200
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Section INRMP Goal INRMP Ensure ade
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Section INRMP Goal Section INRMP Go
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Section INRMP Goal 2009 Conservatio
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Section INRMP Goal Forestry Emphasi
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Section INRMP Goal Forestry Monitor
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Section INRMP Goal Goal Created Sec
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Section INRMP Goal Land Use Minimiz
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Section INRMP Goal Wildlife Monitor
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Section INRMP Goal Wildlife Monitor
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Section INRMP Goal Fisheries Contin
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Section INRMP Goal 2009 Conservatio
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Section INRMP Goal RTLA Provide inf
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Section INRMP Goal GIS Maintain har
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Section INRMP Goal TRI Provide mili
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Section INRMP Goal SRA Instill a se
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2009 Conservation Program Report AD
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2009 Conservation Program Report RT
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Section INRMP Goal Goal Created TRI
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Section INRMP Goal Goal Created 200
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Section INRMP Goal Goal Created 200
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2009 Conservation Program Report FI
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2009 Conservation Program Report FI
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2009 Conservation Program Report Pa
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2. Opening Remarks. COL Weaver welc
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4. Fifteen of the most hazardous fa
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Natural Resources: There was an inf
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2008 Minnesota Statutes 190.25 LAND
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2009 Conservation Program Report BY
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d. Old business e. New business f.
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# of ECS subsections Tax Scientific
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To meet thermoregulatory demands as
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Hillerman, J. P., F. H. Kratzer, an
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Principal Investigator: Dr. John Kr
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3. Determine characteristics used b
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calculated following Kuehn (1985).
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Zielinski, W. J., F. V. Schlexer, K
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2009 Conservation Program Report Na
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Project Title: Training Area 4 Nati
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Project Title: Training Area 8 Borr
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Project Title: Training Area 9 Wild
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Project Title: Training Area 10 Wil
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Listed below is a summery table tha
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Page 244 2009 Conservation Program
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Equal opportunity to participate in
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