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Technical Report No. DRAFT Upper Susitna ATV Stream Crossing Locations Jeffrey C. Davis and David B. Ryland July 2002 Alaska Department of Fish and Game Habitat and Restoration Division Symbols and Abbreviations The following symbols and abbreviations, and others approved for the Système International d'Unités (SI), are used in Habitat and Restoration Manuscripts, Technical Reports, and Special Publications without definition. All others must be defined in the text at first mention, as well as in the titles or footnotes of tables and in figures or figure captions. Weights and measures (metric) centimeter cm deciliter dL gram g hectare ha kilogram kg kilometer km liter L meter m metric ton mt milliliter ml millimeter mm Weights and measures (English) cubic feet per second ft3/s foot ft gallon gal inch in mile mi ounce oz pound lb quart qt yard yd Spell out acre and ton. 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Limited Ltd. et alii (and other people) et al. et cetera (and so forth) etc. exempli gratia (for example) e.g., id est (that is) i.e., latitude or longitude lat. or long. monetary symbols (U.S.) $, ¢ months (tables and figures): first three letters Jan,...,Dec number (before a number) # (e.g., #10) pounds (after a number) # (e.g., 10#) registered trademark ® trademark ™ United States (adjective) U.S. United States of America (noun) USA U.S. state and District of Columbia abbreviations use two-letter abbreviations (e.g., AK, DC) Mathematics, statistics, fisheries alternate hypothesis HA base of natural logarithm e catch per unit effort CPUE coefficient of variation CV common test statistics F, t, χ2, etc. confidence interval C.I. correlation coefficient R (multiple) correlation coefficient r (simple) covariance cov degree (angular or temperature) ° degrees of freedom df divided by ÷ or / (in equations) equals = expected value E fork length FL greater than > greater than or equal to ≥ harvest per unit effort HPUE less than < less than or equal to ≤ logarithm (natural) ln logarithm (base 10) log logarithm (specify base) log2, etc. mideye-to-fork MEF minute (angular) ' multiplied by x not significant NS null hypothesis HO percent % probability P probability of a type I error (rejection of the null hypothesis when true) α probability of a type II error (acceptance of the null hypothesis when false) β second (angular) " standard deviation SD standard error SE standard length SL total length TL variance Var TECHNICAL REPORT NO. DRAFT UPPER SUSITNA ATV STREAM CROSSING LOCATIONS by Jeffrey C. Davis and David B. Ryland Habitat and Restoration Division, Anchorage Alaska Department of Fish and Game Habitat and Restoration Division 333 Raspberry Road, Anchorage, Alaska, 99518-1599 This project was funded by the Alaska Department of Environmental Conservation Non-Point Source Pollution Program. Technical Reports are intended for fishery and other technical professionals. Distribution is to state and local publication distribution centers, libraries and individuals and, on request, to other libraries, agencies, and individuals. This publication has undergone editorial and peer review. The Alaska Department of Fish and Game administers all programs and activities free from discrimination on the basis of sex, color, race, religion, national origin, age, marital status, pregnancy, parenthood, or disability. For information on alternative formats available for this and other department publications, contact the department ADA Coordinator at (voice) 907-465-4120, or (TDD) 907-465-3646. Any person who believes s/he has been discriminated against should write to: ADF&G, PO Box 25526, Juneau, AK 99802-5526; or O.E.O., U.S. Department of the Interior, Washington, DC 20240. i TABLE OF CONTENTS TABLE OF CONTENTS..............................................................................................................................................I LIST OF TABLES .......................................................................................................................................................II LIST OF FIGURES......................................................................................................................................................II ABSTRACT..................................................................................................................................................................1 INTRODUCTION.........................................................................................................................................................1 METHODS....................................................................................................................................................................1 RESULTS & DISCUSSION.........................................................................................................................................3 Summary........................................................................................................................................................................4 LITERATURE CITED................................................................................................................................................17 ii LIST OF TABLES Table 1. Individual parameter and total rank scores for ATV crossing locations. S=single crossing at the location, M= multiple crossings. For specified waters 1=yes and 0=no......................................................10 LIST OF FIGURES Figure 1. Examples of ATV crossings. Numbers are crossing site scores. .................................................................2 Figure 2. Northwest section of ATV sample area showing numbered crossing locations (black dots rank 0 to 3, red triangles rank 4, and red dots rank 5)........................................................................................................5 Figure 3. Southwest section of sample area..................................................................................................................6 Figure 4. Northeast section of sampling area...............................................................................................................7 Figure 5. East section of sampling area........................................................................................................................8 Figure 6. Southeast section of sampling area...............................................................................................................9 1 ABSTRACT The use of All-terrain-vehicles as a means to access off-road locations has increased over the past few years. This use has resulted in numerous stream fords. Stream fords can negatively impact fish directly through damage to incubating eggs and rearing juveniles and disrupting fish migration. Fords cause a loss of fish habitat and can cause increasing bank erosion rates and a loss of water quality through the introduction of fine sediment. This study was conducted to determine the number of stream ford in the Upper Susitna drainage north of the Willow Creek confluence and the upper Peters Creek and Cache Creek drainages. Each crossing was ranked on a scale of 0 to 5 based on the degree of changes to stream channel characteristics and potential for sediment input. There were 158 crossing identified, 49% of these on streams supporting salmon. Forty two percent of the crossings were ranked with site scores of 4 or 5. Key words: All-terrain-vehicles (ATV), sediment, stream fords, off-road-vehicles (ORV), Susitna River, Matanuska-Susitna Borough, Alaska. INTRODUCTION The use of all-terrain vehicles (ATV) has been increasing over the past 10 years. These vehicles are used to access remote property, for hunting and fishing, and for recreation. ATV trails often follow historic trails, winter routes, seismic lines, and electrical transmission lines. ATV trail use, however, has the potential to negatively alter wetland and stream habitats directly and indirectly affecting fish and fish habitat. Direct impacts can occur through damage to spawning redds, disruption of migration and spawning, and direct injury. Indirect impacts can be through changes in water storage and runoff timing, loss of nearshore habitats, migration barriers, and water quality. Information on trail locations, density, and relative impacts are needed to assess impacts to fish habitat and develop recommendations for alternatives to minimize or avoid habitat losses. This study was conducted to begin this process by locating ATV stream crossing locations and evaluate relative fish and fish habitat impacts. METHODS The study area included tributaries to the upper Susitna River. These included Willow Creek north to the Talkeetna River on the east side of the Susitna and the Rabideau, Trapper, Kroto, Peters, and Cache Creek drainages on the west. Surveys were conducted in October of 2001 and June of 2002. ATV crossing were located by flying over the stream drainages in a Helicopter. The latitude and longitude of the locations was recorded using the global positioning system (GPS) and a handheld receiver (Garmin 12XL) and entered on field data sheets. In October, digital videos (Sony TRV 900) were taken of the crossing locations. In June, locations were photographed using digital (Nikon Coolpics 9000) and 35 mm Nikon camera. A Site Score was generated at each site by summing positive site impact parameters ranging from 0 to 5 (Wiedmer 2002). Site impact parameters included the following (Figure 1). Exposed Soil—Visible mineral soil beneath the trail adjacent to the stream. Denuded Banks—All of the vegetation removed from the trail on both banks. Increased Width—Stream width two times greater than natural channel. Surface Erosion—Water pooled or running on the trail surface or evidence of past erosion. 2 Figure 1. Examples of ATV crossings. Numbers are crossing site scores. 3 Bank Alteration—Topography of stream banks altered. Site scores and photographs were used to create the Arcview project (version 3.2) accompanying this report. The photographs are stored on the computer disc with the Arcview project and are stored by site number. The Atlas to the Catalog of Waters Important for the Spawning, Rearing or Migration of Anadromous Fish (ADF&G 1998) was used to determine whether crossings were on specified waterbodies. RESULTS & DISCUSSION A total of 158 stream crossing sites were located within the sample area. The stream crossing locations are shown in Figure 2 through Figure 6. The location and parameter data for each crossing is given in Table 1. The location, ranking data, and photographs are projected on an Arcview project (version 3.2) recorded on the accompanying compact disc. Alternatively, photographs for each site identified on the maps or table can be viewed directly. The photographs on the compact disc have the same name as the crossing location. We found the use of conventional 35 mm camera to produce the best photographs. The digital video created large files that were difficult to manipulate. Also, the quality of still photographs taken from the digital video was poor. The quality of digital photographs was better; however, images were often blurred or missed. Shutter speeds with the digital camera were slow causing blurred photographs when light levels were low. Also the response time (time from when the exposure button was pushed until the exposure taken) was slow often causing repeated attempts to photograph a site. Seventy-eight crossings (49%) were located on specified anadromous waters. Forty-two percent of all crossings were ranked at site scores of 4 or 5. The portion ranked 4 or 5 was the same when evaluating all of the sites or just the anadromous fish streams. Among the scoring criteria, 83% of the sites had exposed soil. This supports our observation that the vegetation on ATV trails is removed after only limited use. This condition suggests that potential impacts to water quality through the introduction of fine sediment occurs early and often in the development of ATV trails. Following exposed soil, bank erosion is the next most common condition observed (63% of the sites). On the west side of the Susitna River most of the crossings area associated with major developed trails (Figure 3). Sites 100 through 115 are located on the extension of Oilwell Road off of Petersville Road. This trail is used primarily to access mines and recreational land. Sites 117 through 126 are located on the trail that runs from Shulin Lake north along Peters Creek to the Petersville Road. Sites 141 through 145 are on the Collinsville Trail near the Three Forks Roadhouse. The approximate location of this trail is shown on the U.S. Geological Survey maps (1:43,000). There may be additional stream crossings on this trail that we did not survey during this project due to weather. Sites 146 through 160 are located on the mining roads of the upper Peters Creek and Cache Creek drainages. Sites 77 through 86 were crossing tributaries to Rabideaux Creek and seemed to be associated with the “Winter Trail” identified on U.S. Geological Survey maps. Trails is this area likely are limited by extensive wetlands. The remaining stream crossings west of the Susitna were associated with trails leading to or around recreational cabin, accessed from either the Parks Highway or Petersville 4 Road. At some locations homeowner associations have formed and constructed ATV bridges at previous ford locations (Figure 7). Crossings on the east side of the Susitna River were not so clearly identified with trails. Sites 75 and 76 are on the Clear Creek Trail, and sites 72 and 73 are on the trail to Larsen Creek. Many of the ATV crossings in the Upper Answer Creek drainage are along the intrastate transmission line. There are a number of crossings located at the bridge where Yoder Road crosses Montana Creek. Most of these crossings appear to be due to recreational ATV riding. Most of the additional crossings in the Montana Creek drainage are where the Middle and South Fork trails cross tributary streams. Sites 25 through 30 are crossings of the North Fork of the Kashwitna and tributary streams. There is what appears to be a hunting trail that travels east along the N.F. of the Kashwitna River. There are a number of crossings of the upper end of Little Willow Creek (sites 35 through 40). Four out of the six of these crossings are ranked either 4 or 5. This portion of Little Willow Creek currently is not specified as a salmon stream; however, recent surveys have identified that area as salmon habitat. These crossings are located on a trail from the Hatcher Pass road east of Willow Mountain. Crossings 49 through 52 cross a tributary to Willow Creek and are located on the Willow Mountain trail. SUMMARY Many of the 160 stream crossings identified in this study are located on well-developed trails. This is particularly true on the west side of the Susitna River. Constructing bridges at these crossing locations, and conducting other trail improvement project on these trails could reduce potential water quality and fish habitat impacts. Although not as clear, crossings east of the Susitna River also appear to be associated with major trails. Additional work needs to be conducted to determine trail location and use. Once locations and potential environmental impacts of trails are known, possible solutions could be investigated such as closing redundant trails, rerouting trails, and building crossing structures. 5 Figure 2. Northwest section of ATV sample area showing numbered crossing locations (black dots rank 0 to 3, red triangles rank 4, and red dots rank 5). 6 Figure 3. Southwest section of sample area. 7 Figure 4. Northeast section of sampling area. 8 Figure 5. East section of sampling area. 9 Figure 6. Southeast section of sampling area. Table 1. Individual parameter and total rank scores for ATV crossing locations. S=single crossing at the location, M= multiple crossings. For specified waters 1 =yes and O=no. "0 Q) IJl ·o .._ c: c: c.. .... Q)(/)"0 :;l: 0 0 :;::;2 c: .Q -ro (j) Q) "0 2 "6J -o Q) c: ~ ~ S ro ~ "0 "0 ·-0 0 ~ > :<;::: Q) ~ Q) '-'-c: ~ > c: 0 ....J ro ~ c: IJl UJ UJ ro ....J o..oQ) ill=~o::: '-"0 0 Q) '+= Q) ·--() 0) Q) x ._ ro c: UJ o'-ro c: f-r:c 1 -149.9238200 62.1998400 1 2 -149.8758300 62.1989300 1 3 -149.7738300 62.2205500 1 4 -149.9509300 62.1824500 1 5 -149.7863500 62.1796100 1 6 -149.7024500 62.1926300 7 -149.987130062.1468600 0 8 -150.0871000 62.0567500 9 -150.0076400 62.1003600 10 -149.9772600 62.0950000 0 11 -149.860560062.1271700 0 12 -149.854460062.1270700 1 13 -149.8281000 62.1307300 1 14 -149.799070062.1361800 15 -149.819140062.1398900 1 16 -149.9743000 62.0514100 0 17 -149.9220600 62.0696600 1 18 -149.9213200 62.0676500 19 -149.780290062.1333000 1 20 -149.7722100 62.1306000 0 21 -149.5734800 62.0674900 0 22 -149.5817500 62.0657800 0 0 0 0 0 0 0 0 0 1 1 1 1 0 0 0 0 1 1 1 1 1 1 1 1 0 0 0 0 0 0 0 0 0 0 1 0 0 0 1 0 0 0 0 0 0 0 1 0 1 1 1 1 1 0 1 1 0 1 1 0 0 0 0 0 0 0 1 0 0 0 1 0 1 0 0 0 1 0 0 1 0 0 0 1 0 0 .!::: 0.. (/) (/) 1 s 1 1 s 1 5 s 0 s 5 s 0 5 s 0 0 s 0 s 1 2 s 0 1 s 0 0 s 0 2 s 0 5 s 0 4 s 0 3 s 0 0 s 1 3 s 2 s 1 3 s 0 s 0 1 s M 10 "0 Q) C/) ·o .._ c: c: c.. .... Q)(/)"0 :;l: 0 0 :;::;2 c: 0 Q) "0 ~ -o Q) c: ·~ ~ S ro ~ "0 "0 -0 0 ~ > :<;::: Q) ~ Q) '-'-c: ~ > ~ (j) ...... "6J c: 0 ....J ...... rn c: rnUJIJ.J ro rooQ)ro rv '-"0 0 Q) ....J o..o Q)=~u.. x ._ ro c: UJ o ._ ro c: f-r:c Q) ~ -() 0) Q) 23 -149.5844400 62.0652500 1 24 -149.6009900 62.0608000 1 25 -149.6266000 62.0577300 1 26 -149.6326900 62.0558800 1 27 -149.6365800 62.0560700 1 28 -149.6419600 62.0573800 29 -149.6543400 62.0582300 30 -149.7084200 62.0620700 1 31 -149.8766000 61.9623000 1 32 -150.0510600 61.9522000 0 33 -150.0669400 61 .9004800 34 -149.9543400 61.9045700 1 35 -149.7066100 61.9631700 0 36 -149.6846900 61.9590200 1 37 -149.6741000 61.9556400 1 38 -149.677 4600 61.95771 00 39 -149.6800900 61.9569900 40 -149.6573900 61.9596100 1 41 -149.678550061.9466600 0 42 -149.6724600 61.9455500 43 -149.6747600 61.9453500 1 44 -149.692900061.9381900 1 45 -149.7514000 61.8984600 46 -149.7463500 61.8758300 0 47 -149.9194400 61.8182800 0 0 1 0 0 0 0 0 1 0 1 1 1 0 1 1 1 0 1 1 1 0 0 0 1 0 1 1 1 1 1 1 1 1 1 0 0 0 0 1 0 1 1 1 1 1 1 0 1 0 1 0 1 0 1 1 1 0 1 1 1 0 1 1 1 0 0 0 0 0 1 1 0 1 1 1 1 1 1 0 0 0 0 0 0 1 0 0 0 0 1 .!::: 0.. (/) (/) 2 s 1 2 s 1 4 s 1 4 s 1 4 s 1 2 M 1 4 s 5 s 0 5 s 1 0 s 1 4 s 1 5 s 2 s 3 s 1 5 s 1 4 s 1 4 s 1 5 s 0 0 s 0 3 s 0 5 s 0 5 s 0 s 0 s 0 s 0 ""0 Q) C/) ·c; -... c c 15.. '- Q) m -o ~ ~ ~ E 2 c .Q Q) ""0 :J -o a> c C/) C/) :J ro :J ""0 ""0 -0 0 ~ ~ > ~ Q) :J Q) '-'-c ~ > ..... -ro U5 "6J c 0 ...J _.C/lcC/lwwro ro o a> ro ~ ._ ""0 0 Q) Q) !E -0 Ol Q) ...J o.o Q)=~u.. x .._ ro c w C.l '-ro c I-OJ 48 -149.933720061.7896600 0 49 -149.8209200 61.8068600 50 -149.8242700 61.8043500 51 -149.7924400 61.8028600 1 52 -149.781640061.8011200 1 53 -150.0781900 62.1040600 0 54 -150.0396200 62.1194100 0 55 -149.9974600 62.1603100 1 56 -149.975410062.1715000 1 57 -149.956400062.1789700 0 58 -149.9505600 62.1909700 1 59 -149.9483600 62.1926000 1 60 -149.9440600 62.2062100 1 61 -149.9477800 62.2057500 .1 62 -149.9523100 62.2070300 1 63 -149.9167200 62.2380000 1 64 -149.915570062.2480700 1 65 -149.9036700 62.2627600 1 66 -149.911020062.2629500 67 -149.9155000 62.2554300 68 -149.9207500 62.2563400 0 69 -149.9128000 62.3105100 1 70 -149.9181000 62.3165200 1 71 -149.9199000 62.3218800 1 72 -149.8616200 62.3572500 73 -149.8569000 62.3650500 0 0 1 1 1 1 1 1 1 0 0 0 0 1 0 0 0 0 0 1 0 1 0 1 0 0 0 0 0 0 1 1 0 1 1 0 1 0 0 0 0 1 0 1 0 0 0 1 1 0 0 0 0 0 0 0 0 0 1 0 1 1 1 1 0 0 1 1 1 0 1 1 1 1 1 1 1 0 1 1 1 1 1 0 0 0 1 0 1 1 1 0 -~ 0. m m 3 s 0 5 s 1 5 M 1 5 s 0 5 s 0 M 1 1 s 1 3 M 2 M 0 s 1 3 s 1 3 s 3 s 0 2 M 0 5 M 0 1 s 0 3 M 0 3 M 0 5 s 0 4 s 0 0 s 0 2 s 1 4 M 0 5 s 0 4 s 1 0 s 11 ""0 Q) C/) ·c; -... c c 15.. .... a> m -o ~ o o ~ $ c .Q Q) ""0 .3 "6J -o -o a> c ~ ~ 3 ro ~ Q) ~ ; e e ~ ~ $ -ro U5 c 0 ...J ro ~ c CllWW ro ...J o.oQ) m=~o:: ._ ""0 0 Q) Q) !E -(.) Ol Q) x ._ ro c w C.l ..._ ro c I-OJ 74 -150.016910062.3846600 0 75 -150.0535800 62.4137500 76 -150.0470900 62.4167700 77 -150.1928500 62.1754300 1 78 -150.219120062.1904500 79 -150.2419400 62.1896600 80 -150.2384800 62.1788000 1 81 -150.260370062.1756400 0 82 -150.2659900 62.1758100 83 -150.2649200 62.1831000 0 84 -150.2608500 62.1906700 0 85 -150.2456900 62.2219500 1 86 -150.260410062.2401100 1 87 -150.3487600 62.3068800 88 -150.3600500 62.2667700 0 89 -150.3654100 62.2671600 0 90 -150.4811000 62.2041000 0 91 -150.4786000 62.2056900 0 92 -150.4999900 62.2072600 1 93-150.464480062.2315100 1 94 -149.9495200 62.7068800 1 95 -150.5359000 62.1018900 1 96 -150.6451900 62.0545400 1 97 -150.4926300 62.1910700 98 -150.4886100 62.1881100 101 -150.5354333 62.1037805 1 0 1 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 1 1 0 1 0 0 0 0 0 0 0 1 0 0 0 0 0 1 0 0 0 1 0 0 0 0 0 1 1 0 0 0 0 0 0 1 0 0 1 1 0 0 0 0 1 1 1 1 1 0 1 1 0 1 1 0 0 0 1 0 0 0 .~ 0. m m 0 s 5 s 4 s 4 s 5 s 2 s 2 s 0 s 3 s 2 s 2 s 3 s 1 s 3 s 2 s 2 s 0 s 0 s 2 s 2 s 1 s 5 s 5 s 1 s 1 s 4 s 1 0 0 1 1 0 0 0 0 0 0 0 1 1 1 1 1 0 1 0 1 1 <ll -c :::l -c <ll en ·o --c c 15.. ... (!)' C/) -c :; .Q .Q ::E 2 -c <!lcenen :::lro c .Q ro iJ5 -:::l -c -c -0 0 ~ ~ > ~ <ll :::l <ll ... ... c ~ > ... -c 0 <ll .OJ c 0 ....J ro :g c enUJUJ ro ....J a.o<lllE=~n:: <ll ~ x ... ro c UJ u"-ro c 1-ll) -() Ol <ll .5 0. C/) C/) 102 -150.5569933 62.0915396 1 103 -150.5842072 62.0812781 1 104 -150.5881183 62.0752595 1 105-150.6125638 62.0700189 1 106-150.6218019 62.0603956 1 107-150.6419668 62.0546132 1 108-150.6467353 62.0587169 1 109-150.6581667 62.0583577 1 110 -150.6891784 62.0499738 1 111-150.709514462.0511972 1 112 -150.7255703 62.0434676 1 113-150.758785462.0525660 1 114-150.766879862.0578982 1 115-150.7933246 62.0742973 1 116 -150.8067897 62.0646096 1 117 -150.8686763 62.1540764 1 118-150.8042228 62.1716326 1 119-150.7978765 62.1763853 1 120-150.7231426 62.2243891 1 121 -150.7303289 62.2492849 1 122-150.7261071 62.2512643 1 123-150.724312962.2838953 1 124 -150.6998658 62.3084848 1 125-150.7011749 62.3059958 126-150.7055738 62.3041237 127-150.1851571 62.2851308 1 1 0 1 1 0 1 0 0 0 0 1 1 4 s 0 4 s 1 2 s 1 4 s 0 5 M 0 4 s 1 5 s 1 3 s 1 1 1 1 1 1 1 1 0 1 1 1 1 0 0 1 1 0 1 1 1 0 1 0 0 0 0 0 1 . 1 0 1 1 0 0 0 0 1 1 1 1 1 5 s 0 0 0 2 s 0 1 1 5 s 0 1 1 5 s 0 1 0 3 M 0 0 0 1 s 1 0 0 1 M 0 0 0 2 s 0 1 1 5 s 0 1 0 3 s 0 1 1 5 M 0 1 1 3 s 0 1 0 3 s 0 0 0 2 M 0 1 1 5 M 0 1 1 5 M 0 1 1 5 s 0 1 0 4 s 1 12 <ll -c -c <ll en ·o ~ c c 15.. a; <ll C/) -c ~ .Q .Q ::E --c <ll c en en :::l ro c 0 ~ iJ5 2 .OJ :::l -c -c -0 0 ~ ~ ~ -<ll :::l <ll ... ... c ~ :;::; en c enUJUJ ro ... -c c 0 ....J j R <ll l8 = ~ n:: o .~ x o ._ ro c <ll ~ UJ u~ ro 0>~ 128 -150.1838 7 43 62.2943896 1 129-150.2506521 62.3261258 1 130-150.3257010 62.3666865 1 131-150.329614662.3972791 132-150.3307694 62.4477840 133-150.3411952 62.4789185 0 134-150.3300343 62.5191452 1 135 -150.6204333 62.3503571 1 136-150.6469533 62.3652381 1 137-150.6340247 62.3729625 1 138-150.6241677 62.4095897 139-150.6330882 62.4134307 140-150.632031162.4174861 141 -150.7558212 62.3746275 142-150.7915097 62.3779110 143-150.7967130 62.3785655 144-150.8059664 62.3783082 1 145-150.8506566 62.3767158 1 146-150.7739280 62.4838233 1 147-150.7690990 62.4975612 1 148-150.8160980 62.5367589 149-150.8169456 62.5366891 150-150.8803921 62.5683824 151 -150.8663084 62.5303279 152-150.8679285 62.5289976 1 153-150.9078882 62.5167355 1 c ll) .5 0. 1 0 0 0 0 0 1 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 1 1 1 1 1 1 0 0 0 0 0 1 1 0 0 1 0 1 0 0 0 0 1 0 1 1 1 1 1 0 0 1 0 0 1 C/) (/) 4 s 1 2 s 1 2 s 1 s 2 s 0 0 s 0 1 s 0 3 s 1 0 2 M 0 0 1 s 0 1 2 s 0 0 3 s 0 0 3 s 0 5 s 0 5 M 0 5 M 0 3 M 0 2 s 0 5 s 0 2 s 4 s 2 s 1 0 3 s 1 1 4 s 1 1 5 s 1 1 5 s 1 Q) en "'0 c i5. (jj ·c; ~ c Q) "'0 0 0 E (ij c "'0 Q) (/) Q) c "(i) en ;:j ::;: 0 ;:j "'0 "'0 "C ·-0 0 .::£ ~ ..... ;:j Q) Q) .... .... c (ij "6> ..... ;:j w w ro .... "C en c en 0 Q) U5 c (ij 0 Q) ro .::£ n:: t;:: 0 _J 0.. 0 Q) ·ro c Q) ·u _J X 0 .... ro 0> w I-(0 c Q) c 0.. -U5 (/) 154-150.9083765 62.5152979 1 1 1 1 1 5 s 155 -150.911 0695 62.5140534 1 1 1 1 1 5 s 1 156-150.918284662.5118864 1 1 1 1 1 5 s 1 157-150.918429462.5122940 1 1 1 0 1 4 s 1 158 -151.0212547 62.4145583 1 1 0 1 1 4 s 1 159-151.0281847 62.4237904 1 1 0 1 1 4 s 1 160-151.0312101 62.4246809 1 1 0 1 1 4 s 0 13 Upper Susitna ATV Stream Crossing Locations Alaska Resources Library and Information Services (ARLIS) is making this PDF available online. The Alaska Habitat and Restoration Division has released two PDF versions of this report. The first PDF version lacked pages numbered 15 and 16, but Table 1 appeared correctly formatted on pages 10-13. The "Literature cited" page appeared duplicated with a black-and-white photo as page 14 and with a colored photo as page 17. A second PDF version was also released with better textual formatting, proper page numbering, and without the duplicated "Literature cited" page. However, the columns and rows in Table 1 (on pages 10-16) were out of alignment. This PDF file comprises chiefly the second PDF version, but pages 10-16 with the poorly formatted table were replaced by pages 10-13 in the first PDF. For that reason, this PDF that ARLIS has made available does not have pages 14-16. 17 Figure 7. ATV crossing of Trapper Creek at site 130 showing newly constructed bridge in upper right corner. LITERATURE CITED Alaska Department of Fish and Game. 1998. Catalog of waters important for spawning, rearing or migration of anadromous fishses: Southcentral region resource management region II. Department of Fish and Game, Habitat Division, Juneau, Alaska. Wiedmer, M. 2002. Lower Kenai Peninsula Summer Off-Road Vehicle Trail Streeam Crossings. Alaska Department of Fish and Game, Habitat and Restoration Division, Anchorage, AK. Technical Report (DRAFT). 27p. LITERATURE CITED (Continued) 18 19