Appendix F Detailed Cover Type Tables - USDA Rural Development

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Bemidji – Grand Rapids Biological Assessment and Evaluation Species Wilson’s phalarope Phalaropus tricolor King rail Rallus elegans Route 1 Alternative Route 2 Alternative Route 3 Alternative Species present in vicinity? Determination of effect Species present in vicinity? Determination of effect Species present in vicinity? Determination of effect No documented observations – suitable habitat may be present. Minimal impacts to appropriate wetland habitats would occur as a result from pole placement. Impacts to individuals and appropriate habitat areas will be minimized by spanning wetland areas when possible, applying BMPs to construction in wetlands. Construction restrictions would be in place during active nesting to avoid direct impacts to nest sites. No documented observations ‐ species occurs in southern Minnesota, which is outside of study area. CNF & DRM: May adversely impact individuals, but not likely to result in a loss of viability in the Planning Area, nor cause a trend toward Federal listing. DNR: Not listed. CNF: Not listed. DNR & DRM: No impact. No documented observations – suitable habitat may be present. Minimal impacts to appropriate wetland habitats would occur as a result from pole placement. Impacts to individuals and appropriate habitat areas will be minimized by spanning wetland areas when possible, applying BMPs to construction. Construction restrictions would be in place during active nesting to avoid direct impacts to nest sites. No documented observations ‐ species occurs in southern Minnesota, which is outside of study area. CNF & DRM: May adversely impact individuals, but not likely to result in a loss of viability in the Planning Area, nor cause a trend toward Federal listing. DNR: Not listed. CNF: Not listed. DNR & DRM: No impact. No documented observations – suitable habitat may be present. Minimal impacts to appropriate wetland habitats would occur as a result from pole placement. Impacts to individuals and appropriate habitat areas will be minimized by spanning wetland areas when possible, applying BMPs to construction in wetlands. Construction restrictions would be in place during active nesting to avoid direct impacts to nest sites. No documented observations ‐ species occurs in southern Minnesota, which is outside of study area. CNF & DRM: May adversely impact individuals, but not likely to result in a loss of viability in the Planning Area, nor cause a trend toward Federal listing. DNR: Not listed. CNF: Not listed. DNR & DRM: No impact. No impacts anticipated. No documented observations – species utilizes islands for nesting. No impacts anticipated. No documented observations – species utilizes islands for nesting. No impacts anticipated. No documented observations – species utilizes islands for nesting. Caspian tern Sterna caspia CNF and DNR: Not listed. DRM: No impact. CNF and DNR: Not listed. DRM: No impact. CNF and DNR: Not listed. DRM: No impact. No impacts anticipated. No documented observations – suitable habitat may be present. No impacts anticipated. No documented observations – suitable habitat may be present. No impacts anticipated. No documented observations – suitable habitat may be present. Great gray owl Strix nebulosa Appropriate breeding habitat area would be slightly reduced as a result of forest cutting. Foraging habitat may be increased as open habitats will be created and structures would provide additional hunting perches. Construction restrictions would be in place during active nesting to avoid direct impacts to nest sites. BMPs will be used during construction in wetlands to minimize impacts to these areas. CNF & DRM: May adversely impact individuals, but not likely to result in a loss of viability in the Planning Area, nor cause a trend toward Federal listing. DNR: Not listed. Appropriate breeding habitat area would be slightly reduced as a result of forest cutting. Foraging habitat may be increased as open habitats will be created and structures would provide additional hunting perches. Construction restrictions would be in place during active nesting to avoid direct impacts to nest sites. BMPs will be used during construction in wetlands to minimize impacts to these areas. CNF & DRM: May adversely impact individuals, but not likely to result in a loss of viability in the Planning Area, nor cause a trend toward Federal listing. DNR: Not listed. Appropriate breeding habitat area would be slightly reduced as a result of forest cutting. Foraging habitat may be increased as open habitats will be created and structures would provide additional hunting perches. Construction restrictions would be in place during active nesting to avoid direct impacts to nest sites. BMPs will be used during construction in wetlands to minimize impacts to these areas. CNF & DRM: May adversely impact individuals, but not likely to result in a loss of viability in the Planning Area, nor cause a trend toward Federal listing. DNR: Not listed. July 2010 Summary of Findings Page 7‐7
Bemidji – Grand Rapids Biological Assessment and Evaluation Species Four‐toed salamander Hemidactylium scutatum Red‐backed salamander Plethodon cinerus Green frog Rana clamitans Mountain lion Felis concolor Pine martin Martes americana Route 1 Alternative Route 2 Alternative Route 3 Alternative Species present in vicinity? Determination of effect Species present in vicinity? Determination of effect Species present in vicinity? Determination of effect No documented observations – suitable habitat may be present. This species is found in mature forests of glacial moraine landscapes where isolated wetlands are abundant. Some habitat loss would occur as a result of upland and wetland forest removal. Impacts to individuals and appropriate habitat areas will be minimized by spanning isolated wetlands, to the extent practicable. BMPs will be used during construction in wetlands to minimize impacts to these areas. No documented observations – suitable habitat is present. This species is found in a wide range of forest habitats. Some habitat loss would occur as a result of forest removal. No documented observations – suitable habitat may be present. Impacts to individuals and appropriate habitat areas will be minimized by spanning wetlands, to the extent practicable. BMPs will be used during construction in wetlands to minimize impacts to these areas. No documented observations – suitable habitat may be present. Appropriate habitat area would be slightly reduced as a result of forest cutting, which would increase habitat for primary prey species. No documented observations – suitable habitat may be present. Appropriate habitat area would be slightly reduced as a result of forest cutting, which would increase habitat for primary prey species. CNF, DNR & DRM: May adversely impact individuals, but not likely to result in a loss of viability in the Planning Area, nor cause a trend toward Federal listing. CNF and DNR: Not listed. DRM: May adversely impact individuals, but not likely to result in a loss of viability in the Planning Area, nor cause a trend toward Federal listing. CNF & DNR: Not listed. DRM: May adversely impact individuals, but not likely to result in a loss of viability in the Planning Area, nor cause a trend toward Federal listing. CNF: Not listed. DNR & DRM: May adversely impact individuals, but not likely to result in a loss of viability in the Planning Area, nor cause a trend toward Federal listing. CNF & DNR: Not listed. DRM: May adversely impact individuals, but not likely to result in a loss of viability in the Planning Area, nor cause a trend toward Federal listing. No documented observations – suitable habitat may be present. This species is found in mature forests of glacial moraine landscapes where isolated wetlands are abundant. Some habitat loss would occur as a result of upland and wetland forest removal. Impacts to individuals and appropriate habitat areas will be minimized by spanning isolated wetlands, to the extent practicable. BMPs will be used during construction in wetlands to minimize impacts to these areas. No documented observations – suitable habitat is present. This species is found in a wide range of forest habitats. Some habitat loss would occur as a result of forest removal. No documented observations – suitable habitat may be present. Impacts to individuals and appropriate habitat areas will be minimized by spanning wetlands, to the extent practicable. BMPs will be used during construction in wetlands to minimize impacts to these areas. No documented observations – suitable habitat may be present. Appropriate habitat area would be slightly reduced as a result of forest cutting, which would increase habitat for primary prey species. No documented observations – suitable habitat may be present. Appropriate habitat area would be slightly reduced as a result of forest cutting, which would increase habitat for primary prey species. CNF, DNR & DRM: May adversely impact individuals, but not likely to result in a loss of viability in the Planning Area, nor cause a trend toward Federal listing. CNF and DNR: Not listed. DRM: May adversely impact individuals, but not likely to result in a loss of viability in the Planning Area, nor cause a trend toward Federal listing. CNF & DNR: Not listed. DRM: May adversely impact individuals, but not likely to result in a loss of viability in the Planning Area, nor cause a trend toward Federal listing. CNF: Not listed. DNR & DRM: May adversely impact individuals, but not likely to result in a loss of viability in the Planning Area, nor cause a trend toward Federal listing. CNF & DNR: Not listed. DRM: May adversely impact individuals, but not likely to result in a loss of viability in the Planning Area, nor cause a trend toward Federal listing. No documented observations – suitable habitat may be present. This species is found in mature forests of glacial moraine landscapes where isolated wetlands are abundant. Some habitat loss would occur as a result of upland and wetland forest removal. Impacts to individuals and appropriate habitat areas will be minimized by spanning isolated wetlands, to the extent practicable. BMPs will be used during construction in wetlands to minimize impacts to these areas. No documented observations – suitable habitat is present. This species is found in a wide range of forest habitats. Some habitat loss would occur as a result of forest removal. No documented observations – suitable habitat may be present. Impacts to individuals and appropriate habitat areas will be minimized by spanning wetlands, to the extent practicable. BMPs will be used during construction in wetlands to minimize impacts to these areas. Yes – 1 CNF documented observation. Appropriate habitat area would be slightly reduced as a result of forest cutting, which would increase habitat for primary prey species. No documented observations – suitable habitat may be present. Appropriate habitat area would be slightly reduced as a result of forest cutting, which would increase habitat for primary prey species. CNF, DNR & DRM: May adversely impact individuals, but not likely to result in a loss of viability in the Planning Area, nor cause a trend toward Federal listing. CNF and DNR: Not listed. DRM: May adversely impact individuals, but not likely to result in a loss of viability in the Planning Area, nor cause a trend toward Federal listing. CNF & DNR: Not listed. DRM: May adversely impact individuals, but not likely to result in a loss of viability in the Planning Area, nor cause a trend toward Federal listing. CNF: Not listed. DNR & DRM: May adversely impact individuals, but not likely to result in a loss of viability in the Planning Area, nor cause a trend toward Federal listing. CNF & DNR: Not listed. DRM: May adversely impact individuals, but not likely to result in a loss of viability in the Planning Area, nor cause a trend toward Federal listing. July 2010 Summary of Findings Page 7‐8
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Appendix F Detailed Cover Type Tabl
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2006). Grassland (Surrogate) Surrog
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upland coniferous forests in the Me
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Table F-1: Vegetation Cover Types w
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Table F-2: Vegetation Cover Type wi
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Table F-4: Vegetation Cover Type wi
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Appendix G Biological Assessment an
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Bemidji - Grand Rapids Biological A
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Avian Mitigation Plan 4.0 OPERATION
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Avian Mitigation Plan Leech Lake Re
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Appendix F Detailed Cover Type Tables - USDA Rural Development

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