Fort RichardsonWetl<strong>and</strong>s comprise approximately 8% (4,990 acres) of Fort Richardson (Lichvar <strong>and</strong> Sprecher 1998b).Wetl<strong>and</strong> types on the post include estuarine, marine, palustrine, riverine, <strong>and</strong> lacustrine. They areclassified as Coastal Halophytic Zone, Lowl<strong>and</strong> Forest Wetl<strong>and</strong>s, Lacustrine Wetl<strong>and</strong>s, Alpine, <strong>and</strong>Subalpine Wetl<strong>and</strong>s.Eagle River Flats is the largest expanse of wetl<strong>and</strong>s at Fort Richardson (2,165 acres). This site was placedon the national priorities list for investigation <strong>and</strong> cleanup of hazardous substances (USARAK 1998).USARAK has not used white phosphorus munitions in wetl<strong>and</strong>s since 1989, when a study was initiated toevaluate the ecological effects of these munitions. USARAK banned the use of white phosphorusmunitions in all impact areas in Alaska in 1991, <strong>and</strong> this explosive is no longer used in any wetl<strong>and</strong>sthroughout the United States. Remediation throughout most of Eagle River Flats is complete, althoughtwo contaminated areas persist. Ongoing monitoring will assist in determining treatment options for theremaining contaminated areas (CRREL 2004).Fort WainwrightApproximately 42% (6,500 acres) of the Main Post is classified as wetl<strong>and</strong>s, with palustrine, riverine, <strong>and</strong>lacustrine types (Lichvar <strong>and</strong> Sprecher 1998a). Bogs, fens, <strong>and</strong> marshes are distributed over the post.Wetl<strong>and</strong>s comprise about 74% (483,500 acres) of Tanana Flats <strong>Training</strong> <strong>Area</strong> (Lichvar <strong>and</strong> Sprecher1998a). Most are classified as Lowl<strong>and</strong> Wet Needleleaf Forest <strong>and</strong> Lowl<strong>and</strong> Forest <strong>and</strong> ScrubThermokarst Complexes.Approximately 17% (42,600 acres) of Yukon <strong>Training</strong> <strong>Area</strong> is classified as wetl<strong>and</strong>s (Lichvar <strong>and</strong>Sprecher 1998a). The prevalent wetl<strong>and</strong> types include Shrub Wetl<strong>and</strong>s, Lowl<strong>and</strong> Wet Needleleaf Forest,Riverine <strong>and</strong> Lacustrine Complexes. Most middle <strong>and</strong> lower portions of north-facing slopes in thewetl<strong>and</strong>/upl<strong>and</strong> complex of Yukon <strong>Training</strong> <strong>Area</strong> are probably wetl<strong>and</strong>s.Donnelly <strong>Training</strong> <strong>Area</strong>Approximately 68% (431,940 acres) of Donnelly <strong>Training</strong> <strong>Area</strong> is wetl<strong>and</strong>s (Lichvar 2000), withpalustrine, riverine, <strong>and</strong> lacustrine types included. The palustrine shrub wetl<strong>and</strong>s are the most commonfound on the training area. The Delta River glaciated lowl<strong>and</strong>s, lower Delta Creek lowl<strong>and</strong>s, <strong>and</strong> upperDelta Creek lowl<strong>and</strong>s ecosections support most of the wetl<strong>and</strong>s on Donnelly <strong>Training</strong> <strong>Area</strong>. Mostwetl<strong>and</strong>s are classified as Lowl<strong>and</strong> Wet Low Scrub <strong>and</strong> Lowl<strong>and</strong> Tussock Scrub <strong>and</strong> Bog Lowl<strong>and</strong> WetForests.3.3.2 Environmental ConsequencesAlternative 1: Continue ITAM Program without a <strong>Management</strong> Plan (No Action)Under the No Action Alternative, ITAM projects would continue to take place without a managementplan or st<strong>and</strong>ard operating procedures. SRA, TRI, RTLA, <strong>and</strong> GIS would continue to have beneficialimpacts to wetl<strong>and</strong>s. GIS would benefit wetl<strong>and</strong>s by providing spatial information important formanaging wetl<strong>and</strong> areas. TRI would benefit wetl<strong>and</strong>s by ensuring wetl<strong>and</strong>s protection does not interferewith training needs. Environmental limitations maps would continue to be used to make militarypersonnel aware of sensitive areas to avoid. SRA, RTLA, <strong>and</strong> LRAM impacts are discussed below._____________________________________________________________________________________________Environmental AssessmentUnited States Army Alaska, <strong>Integrated</strong> <strong>Training</strong> <strong>Area</strong> <strong>Management</strong> Program<strong>Management</strong> Plan 31
SRAThrough the SRA program, soldiers would be educated on the types of activities that require a permit,including depositing soil or other materials into wetl<strong>and</strong>s, extracting water from wetl<strong>and</strong>s, refraining fromdigging in wetl<strong>and</strong>s, <strong>and</strong> projects taking place in or near wetl<strong>and</strong> areas. Environmental limitations mapswould continue to be distributed to soldiers so they would be aware of sensitive areas, including wetl<strong>and</strong>s.RTLARTLA would benefit wetl<strong>and</strong>s by monitoring wetl<strong>and</strong>s use to prevent prohibited activities in thesesensitive habitats <strong>and</strong> to assess the effectiveness of rehabilitation efforts. Military training activity <strong>and</strong>damage to wetl<strong>and</strong>s would be tracked, recorded annually, <strong>and</strong> submitted to the U.S. Army Corps ofEngineers if the five-year wetl<strong>and</strong>s permit is renewed. Recreational impacts to wetl<strong>and</strong>s would also bemonitored under RTLA.LRAMWetl<strong>and</strong>s restoration under LRAM would have beneficial impacts. Wetl<strong>and</strong>s restoration would includereturning the soils, hydrology, vegetative community, <strong>and</strong> biological habitat to a natural condition to theextent practicable. This may require the use of biological <strong>and</strong> chemical controls to control undesirableplant species <strong>and</strong> pests. Use of biological controls, such as predator or parasitic species, would beimplemented where available <strong>and</strong> feasible.Road hardening, road crossings <strong>and</strong> maneuver trail upgrades would benefit wetl<strong>and</strong>s by improving roadconditions. This would encourage drivers to remain on the road <strong>and</strong> out of wetl<strong>and</strong> areas. Drivers aremore likely to remain on roads if they are in good condition.Other LRAM projects are located so as to avoid wetl<strong>and</strong>s whenever possible. Some LRAM activities,however, would have adverse impacts to wetl<strong>and</strong>s if they cannot be avoided. These impacts includegravel pit development <strong>and</strong> mechanical cutting <strong>and</strong> clearing. This impact is considered minor adverse dueto USARAK’s preference to avoid wetl<strong>and</strong>s for construction projects. Required permits would be securedprior to any dredging or filling of wetl<strong>and</strong>s.Alternative 2: Implement ITAM Program through a <strong>Management</strong> Plan (Proposed Action)Impacts to wetl<strong>and</strong>s from Alternative 2 would be similar to those described under Alternative 1. St<strong>and</strong>ardprocedures for all ITAM programs identified in the USARAK ITAM <strong>Management</strong> Plan will provideconsistent <strong>and</strong> efficient work practices. This may improve wetl<strong>and</strong>s by ensuring that contractorsperforming the work would adhere to the st<strong>and</strong>ard procedures designed to protect <strong>and</strong> restore wetl<strong>and</strong>areas.Alternative 3: Suspend ITAM ProgramUnder Alternative 3, ITAM activities would not continue on USARAK installations. This action wouldhave severe adverse impacts to wetl<strong>and</strong>s. The greatest impacts would result from maneuver vehicledamage if soldiers <strong>and</strong> trainers did not avoid sensitive wetl<strong>and</strong> areas. Disturbed wetl<strong>and</strong>s would notundergo remediation.The following table presents a summary of qualitative impact to wetl<strong>and</strong>s resulting from each alternative.Descriptions of the qualitative terms are provided in Chapter 2, Description of Proposed Action <strong>and</strong>Alternatives._____________________________________________________________________________________________Environmental AssessmentUnited States Army Alaska, <strong>Integrated</strong> <strong>Training</strong> <strong>Area</strong> <strong>Management</strong> Program<strong>Management</strong> Plan 32
- Page 1: DEPARTMENT OF THE ARMYUNITED STATES
- Page 5 and 6: TABLE OF CONTENTSCHAPTER 1: PURPOSE
- Page 7 and 8: Table 3.9 Summary of Impacts to Hum
- Page 9 and 10: and Training Land Program, the rang
- Page 11 and 12: • Establish a defined land condit
- Page 13: Donnelly Training AreaDonnelly Trai
- Page 17 and 18: determine whether additional NEPA a
- Page 19 and 20: Table 2.2 Summary of Environmental
- Page 21 and 22: CHAPTER 3: DESCRIPTION OF THE AFFEC
- Page 23 and 24: Maneuver Trail Maintenance and Upgr
- Page 25 and 26: Mungoven 2001). Engineering soil ty
- Page 27 and 28: projects and would result in wide,
- Page 29 and 30: growth. Wind and sand fences would
- Page 31 and 32: iological impacts of military train
- Page 33 and 34: willow scrub communities are common
- Page 35 and 36: disturbed. Further, hardening low w
- Page 37: disturbance or removal, best manage
- Page 41 and 42: Ship Creek (from the Glenn Highway
- Page 43 and 44: effective site drainage. Required p
- Page 45 and 46: Game 1998). More information on wil
- Page 47 and 48: Fort Wainwright and associated land
- Page 49 and 50: Long-term beneficial impacts to wil
- Page 51 and 52: 1998).The Alaska Interagency Wildla
- Page 53 and 54: Prescribed burns, mechanical thinni
- Page 55 and 56: unplanned fires, soldiers are direc
- Page 57 and 58: USARAK also implemented the USARTRA
- Page 59 and 60: LRAM projects beneficial to public
- Page 61 and 62: Cumulative ImpactsPast military act
- Page 63 and 64: Two surveys conducted on Yukon Trai
- Page 65 and 66: LRAM activities under Alternative 1
- Page 67 and 68: 3.9.1 Affected EnvironmentFort Rich
- Page 69 and 70: SRA program, which educates soldier
- Page 71 and 72: 3.10.2 Environmental ConsequencesAl
- Page 73 and 74: Fort Richardson receives few compla
- Page 75 and 76: Table 3.11 Summary of Impacts 1 to
- Page 77 and 78: oads and hauling fill and rock mate
- Page 79 and 80: CHAPTER 4: PREPARERS AND CONTRIBUTO
- Page 81 and 82: Benson, A.M. 1999. Distribution of
- Page 83 and 84: Neely, R. J. 2001. Early Mining His
- Page 85 and 86: CHAPTER 6: AGENCIES AND INDIVIDUALS
- Page 87 and 88: Project NameBulldog TrailWidening P
- Page 89 and 90:
Project NameYukon TrainingArea Demo
- Page 91 and 92:
Project NameYukon TrainingArea Firi
- Page 93 and 94:
Project NameEddy Drop ZoneVegetatio
- Page 95 and 96:
Project Name33 Mile LoopRoad Shortc
- Page 97 and 98:
APPENDIX B: BEST MANAGEMENT PRACTIC
- Page 99 and 100:
Sediment Trap(Permanent) SeedingSil
- Page 101 and 102:
APPENDIX C: SAMPLE RECORD OF ENVIRO
- Page 103 and 104:
APPENDIX D: ITAM PROJECT ASSESSMENT
- Page 105 and 106:
Fire ManagementYes No□ □ Could
- Page 107 and 108:
APPENDIX E: AGENCY COMMENTSThe foll
- Page 109 and 110:
___________________________________
- Page 111 and 112:
___________________________________
- Page 113 and 114:
Sent: Monday, June 13, 2005 5:00 PM
- Page 115 and 116:
Second paragraph - I do not underst
- Page 117 and 118:
sentence could read, "The trees are
- Page 119 and 120:
The third paragraph seems too speci
- Page 121:
USARAK does not have a current five