Loading...
HomeMy WebLinkAboutAttachment_D_Project_Narrative1 Washington Forest Stewardship Plan I. Cover Page Landowner Information Name: King County Housing Authority c/o Patrick Malloy Address: 600 Andover Park W., Tukwila, WA 98188 Phone: 206-574-1139 Email: patrickm@kcha.org Property Information Acreage: 45.49 acres (16.12 forested and 29.37 home site) (22.19, 1.41, .68, 11.41, 9.8) County: King Legal Description:  LOT 1 OF RENTON SP LUA-08-137- SHPL REC #20100111900006 SD SP LOCATED IN W 1/2 OF 32- 23-05,  TR C-2 OF CITY OF RENTON BLA# LUA17-00002 & LND30-0380 REC# 20170511900004 SD BLA LOCATED IN W 1/2 OF STR 32-23-05,  TRACT A OF RENTON SP LUA-08-137- SHPL REC #20100111900006 SD SP LOCATED IN W 1/2 OF 32-23-05,  TR C-1 OF RENTON SP LUA-08-137- SHPL REC #20100111900006 SD SP LOCATED IN W 1/2 OF 32- 23-05,  POR OF SE 1/4 OF SE 1/4 OF NW 1/4 TGW POR OF NE 1/4 OF SW 1/4 - BEGIN SE CORNER OF NW 1/4 TH S 89-26-37 W 40.02 FT TO WLY RIGHT OF WAY FOR STATE ROUTE 515 AND POB TH N 01- 26-10 E 210.13 FT TO S LINE OF N 269.41 FT OF S 479.41 FT OF SAID NW 1/4 TH S 89-44-31 W 93.88 FT TH S 65-51-56 W 51.22 FT TH S 89-26-37 W 80 FT TH S 49-38-17 W 54.67 FT TH S 26-50- 38 W 56.39 FT TH S 89-26-37 W 20 FT TH S 01-26-10 W 105 FT TO SOUTH LINE OF NW 1/4 TH S 89-26-37 W 792.19 FT TH S 01-20-07 W 176.50 FT TH S 89-26-35 W 176.50 FT TO EAST LINE OF W ONE FOOT OF NE 1/4 OF SW 1/4 TH S 01-20-07 W 161.25 FT TO S LINE OF N 1/2 OF N 1/2 OF NE 1/4 OF SW 1/4 TH S 89-35-01 E 400.19 FT TO E LINE OF W 401 FT OF NE 1/4 OF SW 1/4 TH N 01- 20-07 E 55.73 FT TO A POINT BEARING N 87-40-12 W 912.26 FT AND S 01-26-23 W 329 FT FROM NE CORNER OF SW 1/4 TH S 87-40-12 E 872.66 FT TO WLY R/W FOR STATE ROUTE 515 TH N 01- 26-23 E 326.98 FT TO POB --- AKA LOT B OF K C BOUNDARY LINE ADJ APPLICATION NO S 92L0098 APPROVED JUNE 26, 1992 Parcel Numbers: 3223059361, 3223059363, 3223059020, 3223059364, 3223059070 Street Address or Location Description:  18100 107th Place SE, Renton, WA, 98055  10771 SE 184th Lane, Renton, WA 98055 2 Plan Preparer Name: Jason Saura Title: Forest Stewardship Program Coordinator Affiliation: King Conservation District Address: 800 SW 39th Street, Suite 150, Renton, WA 98057 Phone: 425-282-4814 Email: Jason.saura@kingcd.org Plan Preparation Date: April 2024 3 II. Landowner Objectives Long term objectives (10-20+ years)  Manage forest to ensure long-term forest, stream health.  Promote biodiversity.  Maintain a healthy and diverse wildlife habitat.  Foster cooperative stewardship with adjacent landowners and improve usability and enjoyment of the site. Short term objectives (0-10 years)  Remove invasive species (Scotch broom, Himalayan blackberry, English ivy, etc.).  Encourage a diversity of understory shrubs in the forest for wildlife use, invasive species control, recreation, and aesthetics. This would include flowering plants for pollinators/aesthetics as well as thorny plants to discourage access to certain social trails.  Plant native trees and shrubs appropriate to the conditions (full sun, sandy soil, slopes).  Attract a diversity of birdlife to the property.  Remove trash from forested areas.  Improve slope stabilization.  Create and maintain accessible trails for recreation.  Manage existing trees near residences to minimize windfall and wildfire risk.  Allow residents to organize volunteers to assist in maintenance of the forest stands. 4 III. Introductory Overview of the Property Brief Overview of Land Uses in the Vicinity The Vantage Glen property is a King County Housing Authority property with 164 mobile homes for people 55 years of age or older. It is about 13 acres of forest on three sides of 23 acres of home sites. Vista Heights is also a KCHA property with 30 homes. It is 9.8 acres split between forest (Stand 7, 3.3 acres) and home sites (6.5 acres). There is a mapped erosion hazard on the slopes leading down to Panther Creek. Located in Renton’s Benson Hill neighborhood, the area around is very developed. The three properties just to the west of the housing development are forested but on the north side is another housing authority property as well as a shopping center and gas station. To the east are single family homes on .2 acre lots. To 5 the south is another housing authority property and more single family homes with wooded areas along Panther Creek. Vantage Glen is about 1.5 miles east of State Route 167 and 2 miles south of I-405. Topography The Vantage Glen homesites sit in a basin of slopes, surrounding it on all sides. The highest point is in the southwest corner at 475 feet above sea level and the lowest is at 350 ft. The slope is relatively consistent on all sides at approximately 35%. On either side of Panther Creek the slope is much steeper at approximately 65%. There are two terraces that double as walking paths along most of the slope. Access The Vantage Glen property can be accessed from SE 180th St. The roads are paved and well-maintained. The forested areas can be accessed between homesites. Vista Heights can be accessed from SE 184th Lane, just off of 108th Ave SE/515. The forested area near Vista Heights is accessible through a locked gate at the end of the lane. General Forest and Property Description The property can be divided into seven stands that range in size from .96 acres to 3.45 acres. With the exception of Stands 2 and 6, they are forested and have a good diversity of conifer and hardwood species appropriate to the area: Douglas fir, red alder, Big-leaf maple, and Western red-cedar. The trees have an overall good level of health but might be considered overcrowded. The understory species in include sword fern, salal, and Oregon grape and ranges from sparse to medium coverage. A soft layer of duff from 2-6 inches deep covers most of the forest floor. In Stands 1,3, and 5, canopy coverage ranges from 80-90% in most stands with 30-49 year old Douglas fir of 6-10 inch DBH dominating. They have moderate presence of invasive species. Panther Creek runs through the southwest corner of the property, crossing through Stand 4 and Stand 7. There is a mapped erosion hazard on either side of the Creek, as the slope is about 65%. In addition, there are two areas in Stand 4 mapped as aquatic habitat. The trees in Stands 4 and 7 are more likely 50-99 years old and have an average DBH of 11-20 inches. The canopy cover is about 90% with variable tree spacing of 15-20 feet. Both stands have only 10% invasive coverage. Stands 2 and 6 are unique in that they are largely unforested and have extensive (60-80%) invasive coverage. Stand 2 (2.55 acres) is very exposed and dry. The canopy cover is 20% with Douglas-fir, big-leaf maple, and some large Pacific madrone in patches with tree spacing that averages about 30 ft. growing mostly along the bottom of the slope. The Douglas-firs average 30-49 years old with a DBH of 11-20 inches and about 80% crown ratio. They seem overall healthy and the other native trees are about the same age and size class. The middle and upper slopes are grass or moss dominated by Scotch broom and Himalayan blackberry with small patches of English ivy, English hawthorn, English holly, European mountain ash, and non-native cherry scattered throughout. The soil seems dry and sandy along most of the upper slope and more compacted along the two terraces that traverse the stand. 6 Stand 6 is also very exposed and underplanted with 41-60% invasive coverage. The west section of the stand has English ivy and non-native cherry among few big-leaf maple, Douglas-fir, and red alder. The big-leaf maple and Douglas-fir (70% crown ratio) average 30-49 years old with a DBH of 11-20 inches. They seem overall healthy and the other trees are younger and smaller. However, the majority of the stand is dominated by large areas of Himalayan blackberry to the east and Scotch broom in the center. English ivy is limited to the forested area on the west side of the stand. Like in Stand 2, there is a terrace/trail that runs through the middle of the stand as it wraps around the hill. The acreage for each stand is as follows: Stand 1 (.96 acres), Stand 2 (2.55 acres), Stand 3 (3.45 acres), Stand 4 (2.87 acres), Stand 5 (1.31 acres), Stand 6 (1.41 acres) and Stand 7 (3.3 acres). (More detailed stand descriptions to follow under Resource Category 4) Property Corners and Boundaries There is a fence on all sides of the property. There is an additional fence (degraded in some sections) running along the slope on the East side of Panther Creek. Land Use/Forest Management/Timber Harvesting History Up until the 1850s, Renton and the surrounding areas were inhabited solely by the Duwamish peoples. Known as “The People of the Inside,” the Duwamish lived along the Black, Cedar, and Duwamish Rivers & Elliott Bay. European settlement began in the 1850s as a farming community and expanded in the late 1870s to mining coal from Cedar Mountain. Like most of King County, the land also hosted logging operations and was settled more robustly with the railroad in the 1890s. Aerial photos from 1936 show that much of the land was cleared except for a small patch of forest in the northwest corner of the property. The land was used for gravel mining which explains the bowl-shaped property and the sandy soils remaining. Regeneration was evident as early as 1940, with another clearing cut sometime around 1964 that has also since regenerated. The Vantage Glen property was purchased from Burlington Northern Railroad and development started in the late 1970s – to open in 1986. Climate/Weather King County enjoys a mild Pacific maritime climate, which means its weather is heavily influenced by atmospheric conditions over the Pacific Ocean. About two-thirds of the Pacific Northwest precipitation occurs during half of the year from October through March, due to the Pacific storm track, and much of this precipitation is captured in the mountains. Precipitation declines from late spring to early fall with high pressure systems to the west, generally keeping the region fairly dry with pleasant summertime temperatures. On average, King County gets about 46 inches of precipitation every year. As the climate continues changing in King County, we expect more rain and probably more flooding from extreme precipitation events, less snowpack in the mountains lasting into summer, rising sea level along the Puget Sound shoreline and more severe droughts during summer. The prevailing directions of the wind is south or southwest during the wet season and northwest in summer. The average wind velocity is less than 10 m.p.h. 7 Renton experiences an average temperature of 51.8°F, which is higher than the Washington average temperature of 50.47°F and is lower than the national average temperature of 54.45°F. The area where this property is located receives on average 38.36 inches of rain annually and on average has 229 frost free days per year. IV. Resource Description and Management Practices Resource Category 1: Forest Health/Wildfire/Invasive Species (Jason) Forest Health Resource Conditions Insects and diseases: No major forest health problems associated with insects or diseases were observed. In Stand 3 at least a dozen fallen smaller-diameter down Douglas-fir has some evidence of beetles and possible laminated root rot, but the severity of the impact from the pathogen is moderate to low. Environmental Factors: Most of these stands are on a well-drained constructed slope and will likely suffer a little from drought in the summer especially in Stands 2 and 6 which are more exposed. Stands 1 and 3 may benefit from some thinning of Douglas-fir, but not necessary. Animal damage: No significant damage, but moderate woodpecker use of the dead and diseased Douglas- fir in Stand 3 was observed. Forest vegetation, particularly seedlings and young trees are vulnerable to damage from deer and rabbits. Snags and downed logs: Stand 3 has a pocket of many smaller Douglas-fir snags and downed logs. The other stands have a few snags and downed logs. Management Practice General health of the forested areas of the property should be monitored at least twice a year. Monitor all stands for trees that appear unhealthy and check for evidence of insect damage, root disease, or animal damage. A combination of removing invasive plant species and re-planting with native conifer trees is recommended to restore forest health resiliency and reduce future maintenance activities needed to keep forested areas healthy. Stand 1 is mostly medium aged Douglas-fir in relatively good health which may benefit from thinning and understory planting. Stand 2 is very exposed and dry with little forest currently and will require significant planting after invasive species are removed. Stand 3 is dry and stressed on the eastern side, may benefit from thinning and planting of drought resistant trees other than Douglas-firs and understory plants. 8 Stand 4 is mature evergreen forest on steep slope with a stream running through it and will only need to be monitored for now. Stand 5 is mixed conifer and deciduous with some invasives and may need some more conifer and understory plants installed on the upper slope. Stand 6 is very exposed and dry with little forest currently and will require significant planting after invasive species are removed. Stand 7 is mixed conifer and mostly deciduous with some invasive species and could use the addition of some more conifers on the slopes going up to the developed area. Wildfire Resource Conditions The annual frequency and risk of wildfires in western Washington is low compared with eastern Washington. Instead western Washington’s moist conifer forests have historically been confronted with rare, very intense, large, stand replacing wildfires occurring around every 200 years. In western Washington the risk of wildfires starting and damaging structures is closely tied to human activity. Our activities -- such as using gas powered equipment in the woods, having a campfire in our backyard, or lighting off fireworks -- creates many potential ignition sources for a wildfire to start carrying with it a risk of damage to our built infrastructure – homes, sheds, wood fences. The risk of a wildfire spreading once it’s started in western WA is a factor of weather conditions and how built infrastructure and forest vegetation is managed. While we cannot control the weather, we can manage our infrastructure and surrounding vegetation to mitigate the risk of ignition and rate of spread. By actively managing our forests and woods for health we can not only enhance the benefits provided by a healthy forest but also reduce the risk of wildfire and its associated damage. Management Practices The community of Vantage Glen does not fall within the Wildland Urban Interface zone between built infrastructure and forest or natural vegetation as mapped by the WA Department of Natural Resources. As such, this property would not be considered high-risk for wildfire damage. The community falls within the service area of Renton Regional Fire Authority 13. Management practices to protect, enhance, or restore resources: Recommendations to improve wildfire protection and prevention for this property include the following for each zone around the home: 9 Immediate Zone: 0-5 feet from structure  Keep roofs clear of debris, especially in gutters, remove dead vegetation consistently, including needles and leaves  Replace flammable roofing material with fire resistant material such as clay, composite, or metal roofing if possible  Metal and other fire-resistant window frame materials are recommended, since intense conductive and radiated heat can melt vinyl and plastic window frames, providing entry of embers and flames inside. Double-pane windows are recommended  Install 1/8” metal wire mesh screens on vents along the foundation, eaves, and crawlspace, is preferred to prevent embers from entering home  Fireplace chimney screen should be no larger than 1/2” mesh  Keep decks and porches clear of flammable materials, especially underneath (e.g. pine needles, dead leaves, scrap lumber, and firewood)  Create a ‘fire-free’ area within five feet of home or other buildings that has no flammable landscaping materials such as bark mulch or flammable plants that contain resins, oils, or waxes  Trim back tree branches that overhang, touch, or reach close to the house or other outbuildings at least 10 feet back from structures  Consider fire-resistant material for patio furniture and other materials on and under decks and patios  Where there are flammable structures like decks or fences in contact with buildings, consider installing metal flashing or another nonflammable material at the connection point Intermediate Zone 1: 5-30 feet  Mow any lawn areas regularly to 4inches or shorter, especially during fire weather conditions  Within 30 feet of homes, plants should be carefully spaced, low-growing and free of resins, oils and waxes that burn easily  Remove heavy accumulation of woody debris including firewood piles from within this zone if possible  Break continuity of fuels with trails or paths  If fuel tanks are located within this zone, maintain a 5-foot buffer around them with short grass, dirt, or gravel  Prune trees up six to ten feet from the ground (leave at least 2/3 of tree height with live crown) Extended Zone 2: 30-100 feet  Using blue address signs with white reflective numbering and lettering are highly recommended so fire department personnel can more easily find location at night  Remove or redistribute heavy accumulations of woody debris so fuel continuity is broken 10  Prune trees up six to ten feet from the ground while maintaining at least 2/3 of tree height in live crown to create separation between crowns and ground fuels  Monitor and manage forest to improve forest health and resilience to disturbance  Retain large trees  Manage forest for variability of sizes and species By actively managing the forest – removing invasive plants, planting a diversity of trees and shrubs, and thinning as necessary - the health of the forest is improved and the small risk of wildfire and its associated damage is made even smaller. Invasive Species Resource Conditions Stand 1 has less than 20% invasive coverage. There are small patches of English ivy, Himalayan blackberry, Scotch broom, and English hawthorn mostly on the west side of the stand. Stand 2 has 61-80% invasive coverage. There are very few natives here mostly along the bottom of the slope. The middle and upper slopes are dominated by Scotch broom and Himalayan blackberry with small patches of spotted knapweed, tansy ragwort, common tansy, creeping thistle, English ivy, English hawthorn, English holly, European mountain ash, and non- native cherry scattered throughout. Stand 3 has 21-30% invasive coverage which is a moderate amount. There are small patches of Scotch broom, Himalayan blackberry, English ivy, tansy ragwort, creeping thistle, periwinkle, English hawthorn, and English holly mostly on the east side of the stand. Stand 4 has less than 10% invasive coverage with only small patches of Himalayan blackberry scattered throughout. Stand 5 has 21-30% invasive coverage which is a moderate amount. There are small patches of Himalayan blackberry, Scotch broom, English hawthorn, English holly, and non-native cherry scattered throughout. There is also English ivy limited only to the northern part of the stand. Stand 6 has 41-60% invasive coverage which is moderate to high. There are large sections of Himalayan blackberry mostly on the east to middle section of the stand. There is another section that is mostly Scotch broom where the Himalayan blackberry starts to thin out in the middle of the stand. The west section of the stand has English ivy and there are small patches of butterfly bush and non-native cherry. Stand 7 has 10-20% invasive coverage with only small patches of Himalayan blackberry mostly along the north near Stand 3. There is also Himalayan blackberry, English holly, and English laurel in the eastern section behind the locked gate near the roundabout. Management Practices 11  Control invasive species in stand using the best management practices for each species while maintaining adequate ground cover for erosion control.  After removing invasive species, replant the area with native tree seedlings or native shrubs in areas with adequate growing conditions.  Protect vulnerable plantings, like western redcedar or Douglas-fir, from wildlife damage after planting. 12 Resource Category 2: Soils Resource Conditions Table 1: Soil physical properties Soil Type Soil Symbol Parent material Depth to water table Drainage class Depth to hardpan Hardpan drainage rate Water storage Site index and species Soil productivity (ft3 per acre per year) Alderwood gravelly sandy loam, 8-15% slopes AgC Glacial drift and/or outwash over dense glaciomarine deposits 18-37 inches Moderately well- drained 20-39 inches Low: 0- 0.06"/hour Very low (2.7 inches) 111, PSME 157 Alderwood gravelly sandy loam, 15-30% slopes AgD Glacial drift and/or outwash over dense glaciomarine deposits 18-37 inches Moderately well- drained 20-39 inches Low: 0- 0.06"/hour Very low (2.7 inches) 111, PSME 157 Table 2: Soil properties related to forest management Soil Type Symbol Seedling mortality potential Suitability-hand planting Suitability-mechanical planting Suitability- harvesting equipment Suitability- surface site preparation Suitability- deep site preparation Off-road/off-trail erosion potential AgC High: Available water - 1.00 Moderately suited: Rock fragments - 0.50 Moderately suited: Slope/Rock fragments - 0.50 Well suited: Dusty - 0.01 Poorly suited: Rock fragments - 0.50 Well suited Slight AgD Moderate: Available water - 0.50 Moderately suited: Rock fragments - 0.50 Poorly suited: Slope - 0.75, Rock fragments - 0.50 Moderately suited: Slope - 0.50, Dusty - 0.01 Poorly suited: Slope/rock fragments - 0.50 Poorly suited: Slope - 0.50 Moderate: Slope/erodibility - 0.50 Note: The numbers in these tables range from 0.01 to 1.00, indicating the degree of suitability or potentially likelihood. 0.01 indicates that the potential is low or the soil is well-suited for that management activity, while a value of 1.00 means that potential is high or the soil type is unsuited for that management activity. 13 Site Productivity Potential productivity of merchantable or common trees on a site is expressed as a site index and as a volume number. The site index is the average height, in feet, that dominant and codominant trees of a given species attain in a specified number of years. The volume number is the total potential wood fiber volume production on a given site expressed in cubic feet per acre per year. These measures apply to fully stocked, even-aged, unmanaged stands. For this property, site index and volume number are:  Site Index: Douglas-fir 111 at age 50  Volume Number: 157 cu ft./acre/year at age 50 This means that Douglas-fir trees on this site are expected to reach a height of 111 feet by age 50 and produce approximately 157 cubic feet of wood fiber per acre per year. The productivity information for this location comes from the NRCS web soil survey forest productivity report. 14 Site class is an expression of forest site quality based on its potential for growing trees. Each site class is a grouping of site indexes. Douglas-fir sites are broken into five site classes, with class 1 being best for growth. The table below lists the site index ranges for the 5 site classes in western WA. Based on this location’s site index numbers for Douglas-fir, it is a class 3 site, a moderate quality site for growing trees. Site Class Site Index Ranges 1 136 and higher 2 116-135 3 96-115 4 76-95 5 75 and lower Management Practices To protect and enhance forest soil resources, management activities will avoid and limit soil compaction, leave down woody debris after thinning or site preparation, and promptly replant areas that have been site prepped for planting. Equipment use will be avoided when soils are wet in order to minimize soil compaction. Resource Category 3: Water Quality1/ Riparian and Fish Habitat2/Wetlands Resource Conditions Panther Creek runs through the southwest corner of the property through Stands 4 and 7. A fish-bearing stream, it is part of the Black River basin and the Duwamish-Green River watershed. The stream connects to Panther Lake about 1.25 miles to the southeast. There is a mapped erosion hazard on either side of the Creek, as the slope is about 65%. The occurrence of Cutthroat Trout (Oncorhynchus clarki) and Coho Salmon (Oncorhynchus kisutch) has been documented in the Creek according to WDFW’s Priority Habitat and Species Map. In addition, in Stand 4 there are two areas mapped as aquatic habitat. Management Practices Stands 4 and 7 have less than 10% invasive coverage with only small patches of Himalayan blackberry scattered throughout. Any invasive removal would necessitate erosion controls being installed, such as coir logs and jute netting, to avoid landslide and sediment falling into the Creek. The identified wetland areas, while small, are very valuable wildlife habitat features that will be protected and managed carefully. Soils in the stream and wetland areas are more sensitive to damage so access to these areas for forest management activities will be limited to outside the wet season when soils are less saturated and at lower risk of damage caused by management activities. 15 Any invasive species control and removal will be performed in the stream and wetland areas outside of the wet season when soils are not saturated. Resource Category 4: Forest Inventory/Timber/Wood Products (Jason) Resource Conditions Copies of the Forest Rapid Assessment Tool (FRAT) data sheets for all stands are in the Appendix and include a complete species list. The NRCS Web Soil Survey provided additional soil information for all stands: 16  A high seedling mortality rating.  A site index of 111 feet on the Alderwood soil based on a 50 year old Douglas-fir tree: correlates to a Site Class III. Stand 1: Stand 1 from parking lot looking south 17 On the west side of Stand 1 looking east This stand is a long strip along a slope of about 30 degrees with a northern aspect. The trees are mostly mature Douglas-fir with a few red alder, Pacific madrone, western red-cedar, and English hawthorn. The understory is fairly sparse with a mix of native and invasive species present. There are two former roads that start behind the Vantage Glen community center and continue through Stand 2 to the west. The canopy cover is 90% with tree spacing that is clumpy but averages about 15 ft. The Douglas-firs average 30-49 years old with a DBH of 6-10 inches and about 60% crown ratio. They seem overall healthy but a little crowded in some areas. The other trees are younger and smaller. The invasive species cover is about 20% and thickest on the west side near Stand 2 and along the old roads. A soft layer of duff from 2-6 inches deep covers most of the forest floor except along the old roads where it is more compacted. Stand 2: 18 North end of Stand 2 looking south Middle of Stand 2 looking north 19 South end of Stand 2 looking north This stand is a long strip along an artificially constructed slope of about 30 degrees with a western aspect and very exposed. The trees are sparse and mostly along the bottom of the slope consisting of Douglas-fir, big-leaf maple, Pacific madrone, English hawthorn, English holly, European mountain ash, and non-native cherry. The majority of the stand is dominated by large areas of Scotch broom and Himalayan blackberry. There are two former roads that pass parallel from Stand 1 and continue through Stand 3 to the west. The canopy cover is 20% with tree spacing that is patchy but averages about 30 ft. The Douglas-firs average 30-49 years old with a DBH of 11-20 inches and about 80% crown ratio. They seem overall healthy and the other native trees are about the same age and size class. The invasive species cover is about 61-80% and thickest on the upper slopes. The soil seems dry and sandy along most of the upper slope and more compacted along the roads. Stand 3: 20 East side of Stand 3 looking north This stand is a long strip along a slope of about 20 degrees with a northern aspect. The trees are mostly Douglas-fir especially to the east with more big-leaf maple, black cottonwood, western red-cedar, red alder, English hawthorn, and English holly. The understory is fairly sparse with a mix of native and invasive species present. There are two former roads that pass through from Stand 2 and a third former road that starts at the top of the slope and parallels the others. The canopy cover is 80% with tree spacing that averages about 10 ft. The Douglas-firs average 30-49 years old with a DBH of 6-10 inches and about 40% crown ratio. The other native trees are similar age and size class. The upper slope near the southern end of this stand looks like it was restored at some point with mostly hardwoods and shrubs. There is a section where there are a bunch of wind-thrown Douglas-fir with signs of beetle and root rot infestations. The invasive species cover is 21-40% and mostly Scotch broom on the west side near Stand 2 and along the old roads. The invasive species cover transitions to more Himalayan blackberry to the east. A soft layer of duff from 2-6 inches deep covers most of the forest floor except along the old roads where it is more compacted. Stand 4: 21 East side of Stand 4 looking south East side of Stand 4 looking west This stand is a long strip along a slope of about 30 degrees on either side of Panther creek with a mostly eastern aspect. The trees are mostly mature Douglas-fir, big-leaf maple, and western red-cedar. The understory is mostly native shrubs and ferns with only a few invasive species present. The canopy cover is 90% with tree spacing that averages about 20 ft. The Douglas-firs look healthy, average 50-99 years old with a DBH of 11-20 inches and about 70% crown ratio. The other native trees look healthy and are similar age and size class. The invasive species cover is about 10% and mostly Himalayan blackberry near Stand 3. A soft layer of duff from 2-6 inches deep covers most of the forest floor. 22 Stand 5: Middle of Stand 5 looking north This stand is a long strip along a slope of about 20 degrees with an eastern aspect. The trees are a mix of mature Douglas-fir, big-leaf maple, western red-cedar, red alder, English hawthorn, English holly, and non-native cherry. The upper slope is mostly hardwoods and the lower slope is mostly conifers. The understory is a mix of native and invasive species. There is a former road that passes through the stand from north to south. The canopy cover is 90% with tree spacing that is clumpy but averages about 15 ft. The Douglas-firs average 30-49 years old with a DBH of 11-20 inches and about 60% crown ratio. They seem overall healthy but a little crowded in some areas. The big-leaf maple is about the same age and size while the other trees are younger and smaller. The invasive species cover is 21-40% and thickest on the north with English ivy and along the old roads with Himalayan blackberry and the non-native trees. A soft layer of duff from 2-6 inches deep covers most of the forest floor except along the old road where it is more compacted. Stand 6: 23 Middle-west side of Stand 6 looking north Middle-west side of Stand 6 looking east 24 East end of Stand 6 looking west This stand is a long arc along an artificially constructed slope of about 30 degrees with a mostly southern aspect and very exposed. The trees are sparse and mostly along the western end of the stand consisting of big-leaf maple, Douglas-fir, red alder, and non-native cherry. The majority of the stand is dominated by large areas of Himalayan blackberry to the east and Scotch broom in the center. English ivy is limited to the forested area on the west side of the stand. There is a trail that runs through the middle of the stand as it wraps around the hill, but the eastern end of the trail is covered by Himalayan blackberry. The canopy cover is 50% with tree spacing that is patchy but averages about 20 ft. The big-leaf maple and Douglas-fir (70% crown ratio) average 30-49 years old with a DBH of 11-20 inches. They seem overall healthy and the other trees are younger and smaller. The invasive species cover is about 41-60% and thickest to the east of the stand. The soil seems dry and well drained. Stand 7 25 This stand consists of the relatively recently restored slope adjacent to Stand 3 and the housing circle through a flattened area and down a steep slope to Panther Creek and Stand 4. The restored area is mostly deciduous trees consisting of big-leaf maple and black cottonwood and transitions to a more mixed mature deciduous and conifer forest as the stand goes down the slope toward Panther Creek and Stand 4. There is also an open grassy area outside of the fence in the southeast corner that has older Douglas-fir and western red-cedar. There are some invasive species such as Himalayan blackberry, English holly, and English laurel in the southeastern corner of the stand and a patch of Himalayan blackberry in the north of the stand along Stand 3. The canopy cover is about 90% with variable tree spacing of 15-20 feet. The Douglas-fir and western red-cedar look healthy, average 50-99 years old with a DBH of 11-20 inches and 70- 80% crown ratio. The other native trees look healthy and are slightly smaller age and size class. The invasive species cover is about 10% and mostly Himalayan blackberry near Stand 3. A soft layer of duff from 2-6 inches deep covers most of the forest floor. Management Practices In stands 1, 3, 5, and 7, invasive plant control and eradication may be implemented as previously described in the forest health section. In addition to removing invasive plant species in these stands, new native conifer tree seedlings may be re-planted where canopy cover is low or where deciduous trees are declining. If thinning is a possibility in some of the denser areas, that may help the overall health of the forest stand with the large woody material being maintained on site as snags or on the ground for wildlife habitat. Supplemental planting of deciduous native tree seedlings, native shrubs and groundcovers may also be implemented to enhance the understory habitat and in some areas long-term slope stability. Since there may be root rot or bark beetle issues in the Douglas-fir in Stand 3, it is recommended that trees resistant to those be planted in that area. In stands 2 and 6, the same management activities planned for stand 1, 3, 5, and 7 may be implemented where existing forest cover is present. In areas where Himalayan blackberry and English ivy are the dominant vegetation, chemical control is recommended if allowed. Re- forestation activities may then be implemented to re-establish native forest vegetation. These re-forestation activities may include, planting native drought-resistant tree seedlings, maintaining newly planted tree seedlings, amending the soil with mulch, and eventual planting of other trees, native shrubs, and groundcovers. Due to the very small amount of invasive species cover and proximity to Panther Creek in Stand 4, invasive removal work will only be done on the upper slopes. KCHA’s land managers plan on seeking the help of King Conservation District through their Working Lands Initiative to plan, implement, and off-set the cost of some of these management practices. 26 Resource Category 5: Property Access/Roads and Trails Resource Conditions The property can be accessed via SE 181 St off of SE Carr Rd on the northwest and from SE 180 St on the northeast. The roads running through the property are paved and include a parking lot behind the main office at 18100 107th Pl SE. Stand 1 is accessed via a trail behind the office. The trail follows the upper terrace (of two) that was likely formed during earth-moving when the property was developed. The terraces are about 5ft wide, vegetated, and run through Stands 1-3. A similar land-use pattern is in Stand 6 and there is road access through a couple of dead ends road sections or from behind the large KCHA building above the slope. Management Practices It is recommended that the existing terraces be maintained as trails and for access to the forested areas. This will require some invasive plant removal and potentially reseeding and periodic mowing. During forest restoration, the key protection measure will be to avoid soil 27 destabilization on the slopes outside of the existing trails by minimizing access points and replanting after. Resource Category 6: Wildlife Resource Conditions Common Wildlife Species: Only a sample of the 460+ species known to occur in this area Amphibians Birds Mammals Reptiles Western toad N pygmy owl Virginia opossum NW garter snake Pacific giant salamander Great-horned owl Coast mole N. Alligator lizard Pacific tree frog N saw-whet, screech Coyote Western pond turtle W red-backed salamander Barred owl Black bear W. fence lizard Long-toed salamander Dark-eyed junco Cougar Common garter snake Red-legged frog Varied thrush Raccoon American robin Striped skunk Rufous hummingbird Black-tailed deer Anna's hummingbird Porcupine Pileated woodpecker Townsends chipmunk Northern flicker Douglas squirrel Red-breasted sapsucker Bushy-tailed woodrat Hairy & downy woodpecker Deer mouse Cooper’s hawk Mountain beaver American goldfinch Vagrant shrew Black-capped chickadee Richardson's water shrew Chestnut-backed chickadee Hoary bat Common raven Big brown bat Winter wren Little brown bat Red-breasted nuthatch Keen's myotis Crow Silver-haired bat Spotted towhee Hairy-winged myotis House finch Snowshoe hare Golden-crowned kinglet Long-tailed weasel Ruby-crowned kinglet Bobcat 28 Barn swallow Mtn. cottontail Tree swallow Northern flying squirrel Evening grosbeak River Otter Bald eagle Beaver Vaux’s swift Song sparrow Invasive species Bull Frog European starling Norway rat Specific species or evidence of species observed: Amphibians Birds Mammals Reptiles Pacific tree frog Rufous hummingbird Black-tailed deer Pacific giant salamander Chestnut-backed chickadee Racoon Northern flicker Eastern cottontail American robin Coyote American crow Bobcat Pileated woodpecker Eastern grey squirrel Downy woodpecker Townsend mole Barred owl Red fox Dark-eyed junco Red-tailed hawk Forest Habitat Elements Present: Stand 1: This stand contains a mix of mostly taller conifer trees and smaller deciduous trees with an understory of few native and invasive shrubs which provide little wildlife food and cover. Stand 1 contains few dead snags and some coarse woody material. Stand 2: This stand is mostly covered by Scotch broom and Himalayan blackberry and very open with a few non-native trees on the middle to upper slope. The bottom of the slope contains a mix of larger deciduous and conifer trees with an understory of few native and invasive shrubs which provide little wildlife food and cover. There are some smaller snags and downed woody material. Stand 3: This stand is a mix of mostly single-aged conifer on the east side with few native and invasive shrubs. On the west side, the stand is mostly deciduous trees of various ages with a more complex understory of native and invasive shrubs. There are many snags and downed Douglas-fir showing woodpecker use especially on the east side of the stand. Stand 4: This stand is a mix of conifer and deciduous trees of various ages with a dense, complex understory of mostly native shrubs and ferns. There are a moderate amount of snags 29 and downed woody material. Panther creek runs through the middle of this stand which is a fish-bearing stream. Stand 5: This stand is a mix of conifer and deciduous trees of various ages with an understory of a few native and invasive shrubs. There are some dead snags and a small amount of coarse woody material. Stand 6: This stand is mostly covered by Himalayan blackberry and Scotch broom and very open with a few trees on the eastern slope. The west end of the stand contains a mix of deciduous and conifer trees with an understory of few native and invasive shrubs which provide little wildlife food and cover. There are a few snags and a small amount of downed woody material in the forested area to the west. Stand 7: This stand is a mix of conifer and deciduous trees of various ages with a dense, complex understory of mostly native shrubs and ferns. There are a moderate amount of snags and downed woody material. Panther creek runs through the western section of this stand which is a fish-bearing stream. Animal Damage: Deer and rabbit may damage tree seedling plantings, although no evidence of activity have been noted yet. Landowner Objectives for Specific Wildlife Species: Landowners enjoy observing wildlife on and around their properties and would like that to improve but have no objectives for specific wildlife species at this time. Management practices to protect, enhance, or restore resources: Trees species that are planted and are susceptible to deer and rabbit browse, like western red- cedar, may need to be protected with tubes or cages after planting. To protect, enhance, and restore wildlife resources in both stands, a proportion of snags and woody debris may be retained or created in the process of completing the management activities described in Resource Category 4: Forest Inventory/Timber/Wood Products. Standing dead trees provide valuable habitat to the many cavity-nesting species native to western Washington as well as serving as a food source by being home to insects and decay fungi. Branch and brush piles also provide cover and shelter for amphibians, small mammals, and ground-nesting birds. Planting and retaining native fruit- and nut-producing trees and shrubs like cascara, elderberry, salal, and beaked hazelnut may also be considered to enhance wildlife habitat throughout forested areas. Additional Considerations: 30 Wildlife respond to a forest’s vertical layers and horizontal distribution of vegetation (its structure) and the food and shelter it offers (its plant composition). Forest stands that are varied in both structure and composition provide habitat for a broader range of mammals, birds, amphibians and insects. It is these architectural elements and qualities that provide habitats on both coarse and fine scales. This diversity can also be provided by having stands or patches with different structures and compositions adjacent to each other. The following lists are examples of structural and compositional diversity that can occur over time and with planning in all forest types and ages. Structural diversity includes: • Trees of different sizes, ages and shapes • Large old trees • Snags, especially big ones • Large and small pieces of dead wood on the forest floor • Irregular spacing of trees, understory plants and dead wood Compositional diversity includes: • A variety of tree and understory plant species • Hardwood trees • Shrubs, especially bigger, older ones Resource Category 7: Protection of Special Resources & Biodiversity Threatened, Endangered, Candidate Species of Concern and/or Priority Habitat Resource Conditions The occurrence of Cutthroat Trout (Oncorhynchus clarki) and Coho Salmon (Oncorhynchus kisutch) has been documented in Panther Creek according to WDFW’s Priority Habitat and Species Map. In addition, in Stand 4 there are two areas mapped as aquatic habitat. Panther Creek, as it passes through this property, has adequate canopy cover in the riparian area providing shade for cooler temperatures and woody debris for shelter. The water is clear with low levels of fine sediment and diverse, abundant instream cover. This makes it ideal fish habitat. Bank stability might be a continued concern as the slope on both sides of the creek is approximately 60%. Management Practices To maintain slope stability and good conditions for fish species, as trees decline with age they should be replanted as density conditions allow. Invasive plants should be removed before they 31 become a larger problem. Any restoration work on the slope should include slope stabilization best practices such as installing coir logs and jute matting. It might be worth reinstalling the fence along the slope to prevent access to all but resource professionals. Cultural Resources and/or Historical Sites Resource Conditions Based on an analysis of the property in 2023 using the Washington Information System for Architectural and Archaeological Records Data, there are no known archeological and/or historic resource protection issues on this property. The predictive model from the Department of Archaeology and Historic Preservation categorizes the site as moderately low to low risk for archaeological results. Management Practices A formal review, to identify these resources, if any, and their potential protection requirements, will be conducted by the State Department of Natural Resources if and when the landowner proposes to conduct forestry activities that require a DNR-approved Forest Practices Application/Notification. Should cultural resources or historic sites be discovered during installation of any planned practices, work should cease until a qualified site review is performed. If federal payments are related to any installation, work must cease pending evaluation. Washington State laws RCW 27.53 and RCW 27.44 protect all Native American and archaeological sites. For questions about these laws, or to report the discovery of a cultural resource, contact the Office of Archaeology and Historic Preservation in Olympia at 360-586-3065. Forests of Recognized Importance (FORI) Resource Conditions There are no known Forests of Recognized Importance on or adjacent to this property. Management Practices There are no state or federal regulations governing the management of a FORI, thus any actions taken by the landowner would be voluntary. All of the management activities described in this plan will serve to maintain or improve the health of this property and thus contribute to the overall ecological health of the surrounding region. 32 Biodiversity Resource Conditions This property is home to at least seven different native tree species, ten shrub species, and eight herb and forb species. See Appendix B for a full list of species identified by KCD resource specialist. With the exception of Stands 2 and 6, there is good variation in species composition and forest structure throughout the property due to the presence of variable tree spacing, varied overstory tree species and mixed understory light conditions across the forest. Over time this will result in a more uneven-aged and more structurally complex forest, providing valuable habitat to a wider range of wildlife species. Stands 2 and 6 have low diversity of species, being largely covered by invasive Scotch Brook or Himalayan blackberry with scattered individual trees. On the larger landscape, the land is highly fragmented forest broken up by urban development. Vantage Glen’s forested open space is a highly valuable contiguous forest alongside Panther Creek. Management Practices Removing the invasive plants throughout the property, particularly in Stands 2 and 6, and replanting with a wide variety of native trees and shrubs will improve the diversity and health of the forest. Resource Category 8: Aesthetics and Recreation Resource Conditions There is a trail from the main office along the top terrace of the property in Stands 1-4. While currently overgrown with invasive Himalayan blackberry, there is interest in restoring it for access to the forest and recreation. Management Practices Removing the invasive plants along the path will protect, maintain, or enhance the aesthetic, recreational, and educational values or use of the property. As restoration happens, signage could be installed to educate Vantage Glen residents of the process and plan and future of the site. The landowner could also consider adding a trail from the top terrace to the bottom one in a manner that avoids erosion and maintains a safe slope for walkers. 33 Resource Category 9: Carbon Sequestration & Resilience to Climate/Weather-Related Influences Carbon Sequestration Resource Conditions While the climate has always exhibited variability and major climatic shifts have occurred throughout geological history, warming this century is likely to occur 10 times faster than during any climatic shift in the past 65 million years. In the coming century, average annual temperatures in Washington are projected to rise at a rate of 0.2 and 1.0 °F per decade. Although there is more uncertainty in projected changes in precipitation, in general, winters are projected to be wetter and summers are projected to be drier. These changes will most likely effect forest growth over time. It is expected there will be changes to the length of growing season, species (plant and animal) composition and distribution, water availability and duration and an increase in drought conditions during the summer/early fall months. Forests mitigate climate change by reducing the concentration of carbon dioxide, a key “greenhouse gas,” in the atmosphere. As trees grow, they take in carbon dioxide from the atmosphere and, through photosynthesis, release oxygen and create sugars to feed themselves. Through this process, the carbon that was in the atmosphere in the form of carbon dioxide becomes part of the tree’s wood and other tissues. This conversion of carbon dioxide to wood and other solid materials is known as carbon sequestration. Trees will continue to sequester carbon as they grow. When trees are harvested and milled for lumber, the carbon remains sequestered in long-lived wood products incorporated into buildings, furniture, etc. Snags, downed logs, and soil organic matter (the “duff” layer) also provide key long-term carbon storage. Stands 1,3,4, 5, and 7 have canopy coverage that ranges from 80-90% with 6-10 inch diameter Douglas fir at approximately 15ft spacing. The trees have an overall good level of health but might be considered overcrowded. Stands 2 and 6 have small patches of forest along the bottom of the slope and in the northwest corner, respectively. The Douglas-firs average 11-20 inch diameter at 30 ft spacing. The middle and upper slopes are grass or moss dominated by invasive plants. Management Practices Thinning might be recommended, as permitting allows, in the near future in Stands 1 and 3-5 to increase the health and diameter of existing trees for more optimal carbon storage. The forest managers will favor native conifer tree species for any supplemental tree plantings in stands 2 and 6 (pending soil testing) as previously described in this plan. 34 Resilience to Climate /Weather-Related Influences Resource Conditions Most of the forest canopy consists of bigleaf maple and Douglas fir, both trees that are relatively drought tolerant. No signs or drought stress were observed. In the areas with much sandier soils (Stand 2 and 6), the existing Pacific madrone is well suited to droughty conditions. Management Practices As the forest’s current composition is largely drought tolerant, forest managers may just consider increasing the diversity of conifers by planting grand fir in shadier areas and shore pine where full sun conditions exist. Current research indicates that larger, older trees are more efficient at using soil moisture than younger trees, so managing for fewer big trees will result in a more drought-tolerant forest than keeping replanted areas fully-stocked with many young trees. Periodic thinning of young planted or naturally regenerated trees may be needed and implemented by forest managers to achieve this and to reduce potential future drought stress conditions. Stand will be annually monitored for signs of abiotic stress, disease, and insect damage evidence. Stewardship plan will be updated as needed to address changing conditions on site, in region, and as best practices for coping with climate change in our region are recognized. V. Conservation Based Estate/Legacy Planning This property is owned and managed by King County Housing Authority. 35 VI. Management Plan Implementation Timetable Table 3: Management Plan Implementation Timetable Year Management Practice or Activity Location (Stand #) Extent (#, acres, etc.) NRCS Practice Code (if applicable) Comments 2023 Soil testing to determine planting possibilities 2 Complete Forest Management Plan all 2024 Control invasive scotch broom, holly, Himalayan blackberry, and English ivy throughout property All Monitor forest health All 2024 Second pass at controlling invasive scotch broom, holly, Himalayan blackberry, and English ivy All 2024- 2025 Plant native trees and shrubs in areas where invasive removal happened, particularly in Stands 2,5, and 6 2,5,6 Monitor forest health all Formalize and sign soft- impact trail on terrace for community walking access. 1,2,3 2025- 28 Monitor forest health and maintain as necessary with contractor All 2033 Review and update forest plan all 36 VII. Aerial Photo(s)/Property Map(s) Attach copies of aerial photos or maps showing the following: Required - Property boundaries, forest stand types, soil types, location of water bodies, wetlands, and streams, location of roads and skid trails. Optional – Location of property within sections, site class, location of existing and planned recreational trails, topography. 37 VIII. Landowner Signature(s) LANDOWNER SIGNATURE: I/we approve of the contents of this plan and intend to implement the described management activities to the best of my/our ability. _______________________________________________________5/17/2024_____________ _________ Landowner Signature(s) Date __Mary Gonzalez-Hansen______________________________________________________ Print Landowner Name(s) 38 IX. APPROVAL SIGNATURES DNR FOREST STEWARDSHIP PLAN APPROVAL (IF APPLICABLE) This plan meets the requirements for a Forest Stewardship Plan. WA State Department of Natural Resources Authorized Representative Date Print Name Title Address Phone E-mail 39 USDA-NRCS CONSERVATION ACTIVITY PLAN APPROVAL (IF APPLICABLE) This plan meets the requirements for a USDA-NRCS Conservation Activity Plan. Signature of USDA-NRCS Authorized Representative Date Print Name Title Address Phone E-mail 40 Department of Natural Resources and Parks Water and Land Resources Division Office of Rural and Resource Lands 201 So. Jackson St., Suite 600 Seattle, WA 98104 Phone (206) 477-4767 FAX 296-0516 FOREST STEWARDSHIP PLAN ACCEPTANCE FORM OWNERS: MAILING ADDRESS: TAX PARCEL NUMBER: LANDOWNER SIGNATURE: I intend to manage this property in a manner consistent with the objectives specified in the Forest Stewardship Plan, and to implement this plan to the best of my ability. If there is any conflict between this Forest Stewardship Plan and any development regulation applicable to the Property, the most restrictive provision shall apply. Nothing in this Forest Stewardship Plan shall exempt the landowner from obtaining any required permit or approval from King County for any activity or use on the Property. Property owner shall comply with all federal, state or local laws while performing any of the activities or uses on the Property authorized herein. 5/17/2024 Landowner: Date Mary Gonzalez-Hansen KING COUNTY FORESTER SIGNATURE: I have reviewed the Forest Stewardship Plan submitted for long-term management of forestland. This Forest Stewardship Plan adequately describes the natural resources of the site and how they will be managed while conserving forest functions and health. King County Forester Date 41