SBCT Final EIS - Govsupport.us
SBCT Final EIS - Govsupport.us SBCT Final EIS - Govsupport.us
Chapter 5 – Environmental Consequences5.5.10.1.3 Impacts from Live-fire TrainingSignificant Impacts Mitigable To Less Than SignificantImpact 2: Introduction and spread of invasive plants and noxious weeds. The impacts from live-firetraining at SBMR, DMR, PTA, and KTA/KLOA would be expected to affect the introduction andspread of invasive species by potential fires that would put native plant species at competitivedisadvantage. Impacts from noxious weeds under Alternative D would be significant, but mitigable toless than significant.Regulatory and Administrative Mitigation 2: Mitigation measures for effects to noxious weeds fromlive-fire training are the same as those described in under Alternative A.Less Than Significant ImpactsImpacts to vegetation: Vegetation communities within the range areas on SBMR, PTA, andKTA/KLOA would be disturbed by live-fire training. Training would continue at current levels underAlternative D. The majority of the training areas are nonnative vegetation and common native plants,primarily grasses and shrubs, which typically colonize denuded areas quickly and thoroughly. The useof certain types of ammunition increases the chances of starting fires in the impact area and within thesurface danger zones. The potential introduction of fire resulting from the operation of the proposedranges is discussed under Wildfire Management. Impacts to vegetation from live-fire training underAlternative D would be less than significant. Mitigation measures for effects to vegetation from livefiretraining are the same as those described under Alternative A.Impacts to general wildlife and habitats. Impacts to general wildlife and habitats are not expected tochange under Alternative D. Live-fire training would continue to displace various wildlife species.Displacement would be caused by increased human presence in the area, as well as by elevated noiselevels. Wildlife species that are more tolerant of human activity may remain in or around theseranges. Individuals that remain within the impact area and associated surface danger zones could bedirectly affected by ordnance or other munitions. Incidental mortality to wildlife could occur.However, such mortality is not expected to cause measurable impacts to wildlife populations.Training on the new and existing ranges would have a less than significant impact to wildlife andhabitats. Measures described previously under Alternative A would further reduce the impacts of livefiretraining.Impacts to Threatened and Endangered Species: Live-fire training would continue and under the NoAction Alternative, several range improvement projects would occur. Army use of those rangeswould produce a less than significant impact to threatened and endangered species because live-firetraining would occur over a larger area and at more locations. Continued use of Army land fortraining under No Action would prolong the impact to threatened and endangered species. Theseimpacts from continued training would remain a less than significant impact.No ImpactsImpacts to wetlands: No wetlands have been identified at PTA. There is one regulated wetland onSBMR (USACE 2005c). The wetland, located near Mount Kaala, is within the Schofield BarracksForest Reserve where no training activities would occur; therefore, no impacts to wetlands areexpected. On KTA, the one regulated wetland in the training area, Onion Pond, is more than twomiles away from the main training area, and no impacts are expected. A wetland delineation of DMRidentified one jurisdictional wetland (USACE 2002e). This wetland is within DMR but outside of theFebruary 2008 5-226 2/25th SBCT Final EIS
Chapter 5 – Environmental Consequencesarea that will be used for live-fire training. SOPs and BMPs designed to minimize impacts towetlands through stormwater and erosion control would be followed.Impacts from Maneuver TrainingSignificant Impacts Mitigable To Less Than SignificantImpact 3: Introduction and spread of invasive plants and noxious weeds. The impacts from maneuverraining at SBMR, DMR, PTA, KTA, and KLOA would be expected to affect the introduction andspread of invasive species by potential fires that would put native plant species at competitivedisadvantage. Impacts from noxious weeds under Alternative D would be significant, but mitigable toless than significant.Regulatory and Administrative Mitigation 3: Mitigation measures for effects to noxious weeds frommaneuver training are the same as those described in Alternative A.Less Than Significant ImpactsImpacts to vegetation: Vegetation communities within the proposed range areas on SBMR, PTA andKTA, and KLOA would be disturbed by maneuver training. Training with existing vehicles wouldcontinue at current levels. Maneuver training would occur on established roads or trails, as well asareas designated for maneuver training throughout the installations. Vegetation resources would notbe expected to be affected by maneuvers on existing roads and trails. Maneuvers training wouldgenerally occur in unforested areas at PTA and the Keamuku Parcel that contain nonnative vegetationcommunities. Vegetation that would be impacted on SBER and KTA is also primarily nonnative.Impacts to vegetation from maneuver training under Alternative D would be less than significant.Mitigation measures for effects to vegetation from maneuver training are the same as those describedunder Alternative A.Impacts to general wildlife and habitats. No change in impacts to general wildlife and habitats isexpected from the No Action Alternative. Current maneuver training frequency and type wouldcontinue using existing vehicles. Off-road training areas would not expand, so no new habitat losswould occur. Wildlife would continue to be disturbed by noise and human presence during training,but the level of disturbance would not change from existing levels and remain a less than significantimpact.Impacts to Threatened and Endangered Species: Maneuver training would continue and under the NoAction Alternative, several range improvement projects would occur. Army use of those rangeswould produce a less than significant impact to threatened and endangered species because trainingwould occur over a larger area and at more locations. Maneuver training would continue usingexisting equipment and training methods at current off-road training areas. Continued use of Armyland for training under No Action would prolong the impact to threatened and endangered species.These impacts from continued training would remain a less than significant impact.No ImpactsImpacts to wetlands: No impacts to wetlands are expected from maneuver training under AlternativeD. No wetlands have been identified at PTA. There is one regulated wetland on SBMR (USACE2005c). The wetland, located near Mount Kaala, is within the Schofield Barracks Forest Reservewhere no training activities would occur; therefore, no impacts to wetlands are expected. On KTA,the one regulated wetland in the training area, Onion Pond, is more than two miles away from theFebruary 2008 5-227 2/25th SBCT Final EIS
- Page 490 and 491: Chapter 5 - Environmental Consequen
- Page 492 and 493: Chapter 5 - Environmental Consequen
- Page 494 and 495: Chapter 5 - Environmental Consequen
- Page 496 and 497: Chapter 5 - Environmental Consequen
- Page 498 and 499: Chapter 5 - Environmental Consequen
- Page 500 and 501: Chapter 5 - Environmental Consequen
- Page 502 and 503: Chapter 5 - Environmental Consequen
- Page 504 and 505: Chapter 5 - Environmental Consequen
- Page 506 and 507: Chapter 5 - Environmental Consequen
- Page 508 and 509: Chapter 5 - Environmental Consequen
- Page 510 and 511: Chapter 5 - Environmental Consequen
- Page 512 and 513: Chapter 5 - Environmental Consequen
- Page 514 and 515: Chapter 5 - Environmental Consequen
- Page 516 and 517: Chapter 5 - Environmental Consequen
- Page 518 and 519: Chapter 5 - Environmental Consequen
- Page 520 and 521: Chapter 5 - Environmental Consequen
- Page 522 and 523: Chapter 5 - Environmental Consequen
- Page 524 and 525: Chapter 5 - Environmental Consequen
- Page 526 and 527: Chapter 5 - Environmental Consequen
- Page 528 and 529: Chapter 5 - Environmental Consequen
- Page 530 and 531: Chapter 5 - Environmental Consequen
- Page 532 and 533: Chapter 5 - Environmental Consequen
- Page 534 and 535: Chapter 5 - Environmental Consequen
- Page 536 and 537: Chapter 5 - Environmental Consequen
- Page 538 and 539: Chapter 5 - Environmental Consequen
- Page 542 and 543: Chapter 5 - Environmental Consequen
- Page 544 and 545: Chapter 5 - Environmental Consequen
- Page 546 and 547: Chapter 5 - Environmental Consequen
- Page 548 and 549: Chapter 5 - Environmental Consequen
- Page 550 and 551: Chapter 5 - Environmental Consequen
- Page 552 and 553: Chapter 5 - Environmental Consequen
- Page 554 and 555: Chapter 5 - Environmental Consequen
- Page 556 and 557: Chapter 5 - Environmental Consequen
- Page 558 and 559: Chapter 5 - Environmental Consequen
- Page 560 and 561: Chapter 5 - Environmental Consequen
- Page 562 and 563: Chapter 5 - Environmental Consequen
- Page 564 and 565: Chapter 5 - Environmental Consequen
- Page 566 and 567: Chapter 5 - Environmental Consequen
- Page 568 and 569: Chapter 5 - Environmental Consequen
- Page 570 and 571: Chapter 5 - Environmental Consequen
- Page 572 and 573: Chapter 5 - Environmental Consequen
- Page 574 and 575: Chapter 5 - Environmental Consequen
- Page 576 and 577: Chapter 5 - Environmental Consequen
- Page 578 and 579: Chapter 5 - Environmental Consequen
- Page 580 and 581: Chapter 5 - Environmental Consequen
- Page 582 and 583: Chapter 5 - Environmental Consequen
- Page 584 and 585: Chapter 5 - Environmental Consequen
- Page 586 and 587: Chapter 5 - Environmental Consequen
- Page 588 and 589: Chapter 5 - Environmental Consequen
Chapter 5 – Environmental Consequences5.5.10.1.3 Impacts from Live-fire TrainingSignificant Impacts Mitigable To Less Than SignificantImpact 2: Introduction and spread of invasive plants and noxio<strong>us</strong> weeds. The impacts from live-firetraining at SBMR, DMR, PTA, and KTA/KLOA would be expected to affect the introduction andspread of invasive species by potential fires that would put native plant species at competitivedisadvantage. Impacts from noxio<strong>us</strong> weeds under Alternative D would be significant, but mitigable toless than significant.Regulatory and Administrative Mitigation 2: Mitigation measures for effects to noxio<strong>us</strong> weeds fromlive-fire training are the same as those described in under Alternative A.Less Than Significant ImpactsImpacts to vegetation: Vegetation communities within the range areas on SBMR, PTA, andKTA/KLOA would be disturbed by live-fire training. Training would continue at current levels underAlternative D. The majority of the training areas are nonnative vegetation and common native plants,primarily grasses and shrubs, which typically colonize denuded areas quickly and thoroughly. The <strong>us</strong>eof certain types of ammunition increases the chances of starting fires in the impact area and within thesurface danger zones. The potential introduction of fire resulting from the operation of the proposedranges is disc<strong>us</strong>sed under Wildfire Management. Impacts to vegetation from live-fire training underAlternative D would be less than significant. Mitigation measures for effects to vegetation from livefiretraining are the same as those described under Alternative A.Impacts to general wildlife and habitats. Impacts to general wildlife and habitats are not expected tochange under Alternative D. Live-fire training would continue to displace vario<strong>us</strong> wildlife species.Displacement would be ca<strong>us</strong>ed by increased human presence in the area, as well as by elevated noiselevels. Wildlife species that are more tolerant of human activity may remain in or around theseranges. Individuals that remain within the impact area and associated surface danger zones could bedirectly affected by ordnance or other munitions. Incidental mortality to wildlife could occur.However, such mortality is not expected to ca<strong>us</strong>e measurable impacts to wildlife populations.Training on the new and existing ranges would have a less than significant impact to wildlife andhabitats. Measures described previo<strong>us</strong>ly under Alternative A would further reduce the impacts of livefiretraining.Impacts to Threatened and Endangered Species: Live-fire training would continue and under the NoAction Alternative, several range improvement projects would occur. Army <strong>us</strong>e of those rangeswould produce a less than significant impact to threatened and endangered species beca<strong>us</strong>e live-firetraining would occur over a larger area and at more locations. Continued <strong>us</strong>e of Army land fortraining under No Action would prolong the impact to threatened and endangered species. Theseimpacts from continued training would remain a less than significant impact.No ImpactsImpacts to wetlands: No wetlands have been identified at PTA. There is one regulated wetland onSBMR (USACE 2005c). The wetland, located near Mount Kaala, is within the Schofield BarracksForest Reserve where no training activities would occur; therefore, no impacts to wetlands areexpected. On KTA, the one regulated wetland in the training area, Onion Pond, is more than twomiles away from the main training area, and no impacts are expected. A wetland delineation of DMRidentified one jurisdictional wetland (USACE 2002e). This wetland is within DMR but outside of theFebruary 2008 5-226 2/25th <strong>SBCT</strong> <strong>Final</strong> <strong>EIS</strong>