Wolfpen Gap ATV Revisited
Transcription
Wolfpen Gap ATV Revisited
Determining OHV capacity on a watershed scale based on water quality indicators Ouachita National Forest Ouachita National Forest • Est. in 1907 • 1.8 million acres • In Arkansas and Oklahoma • Shortleaf pine and mixed hardwoods • Three ecoregions OHV Carrying Capacity forest-wide and WPG Wolf Pen Gap WPG History • Developed in the early 1990’s • Series of old logging roads connected with trails • Use of the ATV complex grew rapidly • 8,000 to 10,000 riders a year in 1998 • In 1998 a timber sale prompted the first Wolfpen Gap Study • GPS and Stream Surveys User created trails 1998 Legal trails User created trails Subwatersheds BoardCamp Gap Illegal Trail • This trail is about 4’ x .5’ x 200’ • or 14.8 cubic yards • or 20 tons of sediment • or 2 dump truck loads • or 151 acres of clearcut Old Woods Road/Trail • This trail is about 18’ x 3’ x 100’ • or 200 cubic yards • or 270 tons of sediment • or 27 dump truck loads • or 2,037 acres of clearcut Tools and Indicators • Data – water quality – Stream inventories (BASS) – GPS of trails and roads – WEPP data collection • Data – recreation – LEO checkpoints – Use counts • Data manipulation and/or Models – WEPP:Road – sediment values – Aquatic Cumulative Effects – watershed analysis with risk to fisheries Basin Area Stream Survey (BASS) in 1998 • Physical, chemical and biological survey based on stream habitat • In 1998 we compared streams to similar sized reaches and habitats – embeddedness – percent fines and sand – pool volume – maximum pool depth 1998 - 2001 • The Wolfpen Gap area was closed to ATV’s except for authorized roads and trails. • Obliteration of illegal trails and performed road and trail maintenance. • December 2000 WPG trails are closed due to ice storm damage. • The summer of 2001 WPG streams are resurveyed. – There was improvement in physical habitats. – Potential problem with stream biota. Gap Creek Board Camp Creek Brushy Creek Streams Subwatersheds > than 4500 acres Lower subwatersheds Middle subwatersheds Upper subwatersheds Caney Creek Upper Pool Embeddedness 60 50 40 30 20 10 0 Brushy 01 Caney 01 Board 01 Gap 01 Board 98 Gap 98 Species Richness 14 12 10 8 6 4 2 0 Brushy 01 Caney 01 Board 01 Gap 01 Board 98 Gap 98 2001 Recommendations • Continue o Aggressive rehabilitation of riparian areas and illegal trails, o Creating public awareness, and o A continued law enforcement presence. • Close or relocate identified roads and trails, • Harden stream crossings and approaches • Consider limiting the number of ATV users per year, • Consider a seasonal closure limiting ATV use to the dry season (October 15th – April 15th). WPG 2001 - 2005 • WPG was reopened in March 2002 – Built 2 new box culverts stream crossings – Closed one crossing – Constructed ~ 5 miles of road/closure - ~ 3 miles but • Use increased to 17,000 UPY (by 2008), • No trail maintenance • Little road maintenance 2005 and beyond • 2005 – Travel Management Plan – Motorized Public use of roads and trails • • • • 2006 2008 2009 2010 – – – – Re-inventory of streams using BASS MIS report Consultation with F&W service MVUM EA signed 2006 BASS • Physical features back slide – Pool Volume – Surface area – Thalweg depth • Mixed results – from stream unraveling – Embeddedness – % sands and fines Volume 160 140 120 Cubic meters 100 80 60 40 20 0 1996 1996 1998 1998 2001 2001 2001 2001 2006 2006 2006 2006 Brushy Caney Board Gap Board Brushy Caney Gap Board Brushy Caney Gap Creek 50 Creek 60 Camp Creek 90 Camp Creek 50 Creek 60 Creek 90 Camp Creek 50 Creek 60 Creek 90 Creek 70 Creek 70 Creek 70 2008 Management Indicator Species (MIS) report For the Lower Ouachita Mountain Ecoregion • Green sunfish and Central Stoneroller populations are increasing • Orangebelly Darter and Yellow Bullhead populations are declining the reason • OHV use increases and failure to maintain roads are the source? MIS 100 Number of Fish per 100 meters 90 Central Stoneroller in LOM 80 70 60 50 40 30 20 10 0 Ref Mgn All All LOM LOM Ref Mgn 90 90 LOM LOM Ref Mgn 91 91 LOM LOM Ref Mgn 92 92 LOM LOM Ref Mgn 96 96 LOM LOM Ref Mgn 01 01 LOM LOM Ref Mgn 06 06 LOM LOM MIS 100 Number of Fish per 100 meters 90 Central Stoneroller in LOM 80 70 60 50 40 30 20 10 0 Ref Mgn All All LOM LOM Ref Mgn 90 90 LOM LOM Ref Mgn 91 91 LOM LOM Ref Mgn 92 92 LOM LOM Ref Mgn 96 96 LOM LOM Ref Mgn 01 01 LOM LOM Ref Mgn 06 06 LOM LOM MIS 100 Number of Fish per 100 meters 90 Central Stoneroller in LOM 80 70 60 50 40 30 20 10 0 Ref Mgn All All LOM LOM Ref Mgn 90 90 LOM LOM Ref Mgn 91 91 LOM LOM Ref Mgn 92 92 LOM LOM Ref Mgn 96 96 LOM LOM Ref Mgn 01 01 LOM LOM Ref Mgn 06 06 LOM LOM WEPP Road • Allows you to model various road/trail scenarios • Can build a sediment budget related to road design, location, use, surfacing, and maintenance • Allows you to be site specific with relation to climate and soils. • Demonstrated the usefulness of buffers, erosion control devices (wingditches, cross drains, waterbars, etc.) R 23 insloped with rocked ditch R 22 insloped with rocked ditch L19 outsloped unrutted R 23 insloped with bare ditch R 22 insloped with bare ditch L19 outsloped unrutted Output Road Seg L1 L2 L3 L4 L5 L6 L7 L8 L9 L10 L11 L12 L13 L14 L15 L16 L17 L18 L19 L20 Design insloped bare outsloped unrutted insloped bare insloped bare outsloped unrutted outsloped unrutted insloped bare insloped bare outsloped unrutted insloped bare outsloped unrutted insloped bare outsloped unrutted insloped bare insloped bare insloped bare insloped bare insloped bare outsloped unrutted outsloped unrutted Road Road Road grad len Widht % (ft) (ft) 2 4 5 5 4 4 5 8 7 7 7 9 9 9 8 9 1 5 5 5 165 38 143 110 71 143 126 143 165 93 27 44 66 66 99 44 33 105 99 154 13 12 12 13 12 13 13 11 15 13 13 12 12 11 13 15 14 15 14 13 Fill grad % 0.3 70 0.3 0.3 5 0.3 0.3 55 0.3 60 70 0.3 0.3 0.3 65 70 55 55 70 55 Fill len (ft) 1 5 1 1 1 1 1 6 1 5 5 1 1 1 5 10 5 3 6 2 Buff grad % 0.3 0.3 0.3 15 16 10 12 17 10 22 20 0.3 25 22 20 0.3 40 20 10 20 Buff len (ft) 1 1 1 60 35 160 150 100 85 15 10 1 40 120 60 1 12 60 90 150 Precip (in) 56.96 56.96 56.96 56.96 56.96 56.96 56.96 56.96 56.96 56.96 56.96 56.96 56.96 56.96 56.96 56.96 56.96 56.96 56.96 56.96 Sed Road (lb/yr) 1574.41 524.67 2429.69 1835.09 767.56 1617.64 2253.82 4474.84 3134.4 2640.83 524.57 710.03 1158.11 1182.37 3212.21 1975.59 920.48 2611.29 1815.7 2024.36 Sed Profile (lb/yr) 1267.32 386.37 1868.82 636.08 194.75 147.39 334.32 1275.85 357.82 1978.4 355.85 484.03 416.54 274.04 1303.12 1613.38 752.59 1215.75 235.34 457.05 Sediment yields in tons/mile/year– Ouachita Mtn. Ecoregion Use Native surface road Gravel road ATV trail Fireline High 20.8 15.8 23.0 22.6 Moderate 5.5 4.2 6.1 6.0 Low 0.8 0.6 0.9 0.9 Determining Recreation Use • A map – high, medium, and low • LEO and Ranger input • LEO traffic check points – – – – Long term data Distributed across the forest Year round data source Does not capture types of vehicles • Trail counts – timed counts documenting direction and type of vehicle Use levels forest wide OHV use levels OHV use levels Very High Very High High .12,000 UPY Moderate High 8,000 – 12,000 UPY Low Moderate 2,000 – 8,000 UPY Low < 2,000 UPY Example of use counts summer holiday summer weekend summer hunting may - sept weekday season winter/ spring weekend winter weekday LEO checkpoint data Vehicles per day 199 percent of summer holiday number of days 9 95 89 47 23 0 38% 36% 19% 9% 0% 38 85 61 171 Example of use counts summer holiday summer weekend summer hunting may - sept weekday season winter/ spring weekend winter weekday LEO checkpoint data Vehicles per day 199 percent of summer holiday number of days 9 Actual Count date 7/4/2008 16 atvs for a 30 minute count 208 ATVs for a summer holiday 95 89 47 23 0 38% 36% 19% 9% 0% 38 85 61 171 Example of use counts summer holiday summer weekend summer hunting may - sept weekday season winter/ spring weekend winter weekday LEO checkpoint data Vehicles per day 199 percent of summer holiday number of days 9 95 89 47 23 0 38% 36% 19% 9% 0% 38 85 61 171 3,014 6,345 2,427 Actual Count date 7/4/2008 16 atvs for a 30 minute count 1,872 208 ATVs for a summer holiday ATV UPY 16,975 3,316 0 Determining OHV Carrying Capacity for WPG • Use in 1998 lead to damage <8,000 UPY • Line did not want a quota system • From LEO checkpoints and trail counts seasonal limits could be calculated – Summer holidays including weekends= 1,872 UPY – Summer non-holiday weekends = 3,014 UPY – Combined = 4,886 UPY • Consultation with F&WS required trail counts as well seasonal restrictions 2010 Final MVUM EA • 190 subwatersheds (6th level, 12 digit, 10,000-45,000 ac) • 21 subwatersheds were identified as a priorities (OHV, TandE, Mining, Maintenance issues) • Subwatersheds that are currently exceeding sustainable carrying capacity – Three – all in the very high use areas • WPG – Limited season - May 15-Sept 15 weekends only and holidays – 5,000 users per year – Precipitation and Maintenance requirements What worked • Data – water quality – Stream inventories (BASS) – worked on watershed and ecoregion scale – WEPP data collection – provided site specific info • Models – WEPP:Road – allows comparisons of use – Aquatic Cumulative Effects – allows for risk and use comparisons • Data – recreation – LEO checkpoints – surprise data source – Use counts – limited to very high and high use areas i.e. targeted • Models/spreadsheets – Seasonal uses – recreation seasons – Vehicle counts – addresses a larger question of types and direction What did not work • Public buy in • The existing WPG trail system is based on a poor trail design • Need to reinvest in new trails – obliterate old trails • Lack of desire to manage use Yeah but………..