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HomeMy WebLinkAboutLog200 I I I I I I I I I I I I I I I I I I I e e ~~ Geo iiilif!! Engi neers "'~lii"" July 24, 2003 Port Ludlow Associates, Inc. 70 Breaker Lane Port Ludlow, Washington 98365 Attention: Mark Dorsey Landscaping Plan Ludlow Cove Residential Development Port Ludlow, Washington File No. 10622-001-00 INTRODUCTION We are pleased to submit our Landscaping Plan for the Ludlow Cove Residential Development, Port Ludlow, Washington. This landscaping plan has been completed to document the pertinent site information that will be utilized for the Ludlow Cove Residential Development proposed by Port Ludlow Associates, Inc. (PLA). Jefferson County has determined actions that would mitigate any significant adverse impacts on the environment that might otherwise result from the development. Included in their recommendations for the mitigation are buffers along wetlands, streams, shorelines, and the tops of slopes. Areas of open space, critical area enhancement, a beach picnic area and new and existing trails are also important aspects of the mitigation effort. We have identified the extent of the proposed removal of invasive species, debris and topsoil in critical areas. The required wetland restoration, wetland buffer enhancement plan, and shoreline buffer area treatments have been described in detail. Detailed plans for the walking trail and stream crossing have been included in the planting plans. Appendix A is the planting plans, and includes placement of bird boxes, large woody debris and picnic tables. AREAS OF RESTORATION AND ENHANCEMENT Wetland Areas The vegetation in the wetland areas will be disturbed as little as possible by enhancement activities. Historic use of the area between survey point (SP) 2794 and 2795, has resulted in a large pile of brush within the wetland boundary, which has negatively impacted a small area of Wetland #1. The area of impact is shown in photograph 1. The brush that was pushed into the A . E \yetland at thi.s location will be removed and the soil will be left as undisturbed as possible. pphed nVlronmental :Services 1550 Woodridge Dr. SE Port Orchard, WA 98366 Iw.w.geoengineers.com LOG ITEM # ;2tJ tJ Page~~L.~_..Cli:~ Telephone (360) 769.8400 Fax (360) 769.6700 I e e I Port Ludlow Associates, Inc. July 24, 2003 Page 2 I I I Replanting with skunk cabbage (Lysichiton. americanum) and slough sedge (Carex obnupta) will occur in this area. Figure A-2t illustrates the details of the treatments for the wetland and buffer areas. In the disturbed area of Wetland #1 between SP2795 and SP2797, fill will be removed if necessary, clean soil will be brought in and the area will be revegetated with the following wetland species: slough sedge (c. obnupta), willow (Salix commutata), skunk cabbage (1. americanum), and salmonberry (Rubus spectabilis). I I I I I Photograph 1 - Area of Wetland Disturbance I Wetland Buffer Enhancement Plan Based on Subsection 10.507(7) of the Jefferson County Interim Critical Areas Ordinance a stream buffer of 50 feet is required within a "high Intensity Land Use" area. A revision of the modified buffer averaging reduced the buffer on the south side of this stream and increased the buffer on the north side of the stream. A minimum buffer of 25 feet remains on the south side and the total area contained within the streamside buffer after averaging is not less than that contained within the standard buffer prior to averaging. The stream and wetland buffers are shown in Figures A-2. In the previously cleared area from SP2791 to SP2794, the invasive species such as Himalayan blackberry (Rubus armeniacus) will be removed and the buffer will be revegetated with native species such as salmonberry (R. spectabilis) and Indian plum (Oemleria ceras iform is). Salal (Gaultheria shallon), sword fern (Polystichum munitum) and Douglas fir (Pseudotsuga menziesii) will be planted in the drier areas. No clearing or revegetation will be done within the buffer area between SP2797 and SP2798. Between SP2798 and SP2801, near the west stream, selective clearing of invasive species will be done without disturbing or removing the existing sword fern. At the trail crossing of the west stream, from near SP2798 to near SP2931, selective clearing of invasive species, pruning, limbing, and removal of alder will occur. There are numerous logs in this area that are relics of previous use of the property, the majority of which are to remain as large woody debris. I I I I I I I GeoEngineers lOG ITEM ~ ;)...(9 0 Ff3g''- €. j./ "'~ ~ ,; I . ---Plle.No...l062,kOOI-OO I I e e I Port Ludlow Associates, Inc. July 24, 2003 Page 3 I Wetland buffers should be marked with temporary signs at an interval of one per parcel or every one hundred feet, whichever is less. Signs shall remain in place prior to and during approved construction activities. The signs shall contain the following statement: "Wetland and Buffer - Do Not Remove or Alter Existing Native Vegetation." The applicant shall include on the face of the final mylar the boundary of the wetland and its averaged buffer. I I Native Growth Areas The native vegetation theme will be retained for the project. Forested and wetland areas with established native vegetation that have no invasive species will not be disturbed. I I I Shoreline Buffer Areas Shoreline buffers will be created along Port Ludlow Bay of 30 feet from either the Ordinary High Water Line (OHWL) or from the crest of the bank if the bank is over 10 feet high. Berms and large piles of fill located outside the buffer area (located near SP 2923) shall either be removed, landscaped, or modified to conform to natural topography. A large cement structure and logs are located on the shoreline where historically, logs were skidded to the bay. Photograph 2 is of the historic log skidding area. Soil will be brought in to contour the ground and partially cover the exposed vertical face on the landward side of the cement structure. The revegetation of this section of shoreline will consist of the following native species: wild rose (Rosa nutkana), dune grass (Elymus mollis), willow (Salix hookeriana), salt grass (Distichlis spicata), twinberry (Lonicera involucrata), shore pine (Pinus contorta var, contorta), and Douglas fir (P, menziesii). The historical nature of this area will be retained. Figure A-3 is the planting plans for this section of shoreline. I I I I I I I I I I GeoEngineers Photograph 2 - Historic Log Skidding Area. LOG ITEM # '}-.eeJ Page-3_cf File No. 10622-001-00 I I e e I Port Ludlow Associates, Inc. July 24, 2003 Page 4 I I For the vegetation management of the shoreline buffer at Beach Point Picnic Area (Figure A-4) between SP293 I to SP2936, invasive species such as Himalayan blackberry will be removed and revegetated with native species. Species to be used for shoreline revegetation at Beach Point Picnic Area are wild rose (R. nutkana), dune grass (E. mollis), willow (8. hookeriana), salt grass (D. spicata), Douglas aster (Aster subspicatus), twinberry (1. involucrata), and shore pine (P. contorta). Consideration was given to the selection of tree species in this area, in an effort to minimize view obstruction without compromising wildlife habitat. This area will also be supplemented with large woody debris. The vegetation within the shoreline buffer from SP2751 to the southeast property corner at SP2670 will be left undisturbed. I I I I Slope Buffer Areas Impacts to slope stability should be mitigated by observing the required 30-foot minimum buffer. Buffer perimeters shall be marked with temporary signs at an interval of one per parcel or every one hundred feet, whichever is less. Signs should remain in place during construction activities and should state "Landslide Hazard Area and Buffer - Do Not Remove or Alter Existing Native Vegetation." I I Other Wildlife Features Areas of the property contain abundant logs left over from the historical use of the site. A majority of these logs will be left in place to provide habitat, several will be moved to the Beach Point Picnic Area. Bird boxes will be added to the site to provide nesting habitat. Twelve bird boxes will be placed near the trail in the wetland, wetland buffer and stream areas. Figures A-2 and A-5 show placement of bird boxes. Figure A-4 shows placement of large woody debris I I I Walking Trail System An intricate walking trail system exists in the Port Ludlow area. Portions of the walking trail exist on the property along Paradise Bay Road and Oak Bay Road. New trails proposed for the property will be integrated with the existing trails. The new trails will reach to Beach Point Picnic Area and traverse the ravine of the east stream. A picnic area is to be provided for wildlife viewing. The trails will be four feet wide and have a wood chip base. Engineered crossings of streams will utilize pinned piling foundations or floating tire pilings, so that the existing flow is unimpeded and the structure will be esthetically pleasing and ecologically sensitive. Figure 1 is a schematic of a footbridge with a pinned piling foundation. I I I Vegetation The vegetation selected for restoring disturbed areas includes speCIes that mimic the vegetation located within the existing area. Selecting vegetation found in the vicinity of restoration helps to avoid the spread of non-native and undesirable species, such as reed I I GeoEngineers LOG ITI=M # ~o ..... Page~ O{Fite'NO' 10622-001-00 I I e e I Port Ludlow Associates, Inc. July 24, 2003 Page 5 I I canary grass (Phalaris arundinacea), Scots broom (Cytisus scoparius), and Himalayan blackberry (R. armeniacus), and also serves to foster survivability of the planted species. The selection of vegetative species is based also on the hydrologic requirements of the plants and their attributes, such as being able to support wildlife, to improve water quality, and to foster aesthetic appeal. Care should be taken to assure that nurseries provide local planting material and are not obtaining plant material that originates from a different region. It is also important to verify that nurseries are cultivating plant material rather than collecting whole plants from functioning wetlands. All plant material should be obtained from seed stock collected from the Puget Sound Lowlands Eco-Region to help minimize plant mortalities, ensure adaptability, decrease maintenance costs, and preserve local diversity. Containerized, bare-root, or balled and burlapped planting material may be used for establishing shrubs and trees within the mitigation area, depending on time of year and plant availability. Using containerized plants during the growing season will optimize plant survivability due to ease of transportation, and presence of a well-developed and intact root system. Many tree and shrub species are available as bare-root materials during the dormant season (October through March). Bare-root material is generally much less expensive than containerized or balled and burlapped planting material. Plant species selected for the mitigation in relation to the previously mentioned attributes are discussed as follows: . Douglas Fir (Pseudotsuga menziesii): This familiar tree grows well in various soil types, especially in sunny areas. It has flat needles that are sharp-pointed but not prickly, and many medium-sized cones that drop to the ground each fall. The ridged Douglas Fir bark on older trees is fire-resistant because of its thickness. An uncrowded tree has pyramidal crown with dense foliage. Deer and rodents browse on the seedlings, and small birds and mammals eat the seeds. Needs well-drained soil and full sun (Thurston County Conservation District). From extremely dry, low elevation sites to moist mountain sites; on the outer south coast it is replaced by western hemlock except on dry, rocky sites or in areas influenced by fire (Pojar and MacKinnon 1994). . Sitka Spruce (Picea sitchensis): Though more common on the coast, this swampland conifer is well adapted to wet streamside conditions. Sitka Spruce grows quickly and is an easy victim of bud-eating insects. It has bristly, sharp, bluish-green needles on dropping branches and medium-sized reddish cones with irregular scales. Deer, rabbits, and grouse eat its twigs and leaves, and small mammals and birds eat its seeds. It provides good nesting habit and winter shelter for birds (Thurston County Conservation District). In pure or mixed stands, often on moist, well-drained sites such as alluvial floodplains, marine terraces, headlands, recent glacial outwash, avalanche tracks; also on old logs or mounds on boggy sites; typically at low to middle elevations, but reaching I I I I I I I I I I I I I I GeoEngineers LOG ITEM # ~1 Page_of File No. 10622-001-00 I I e e I Port Ludlow Associates, Inc. July 24, 2003 Page 6 I I timberline on the Queen Charlotte Islands and the most maritime parts of southeast Alaska (Pojar and MacKinnon 1994). . Shore Pine (Pinus contorta var. contorta); Short, to 20 m tall (sometimes a straight tree to 30 m); highly adaptable, tolerant of low-nutrient conditions; found from dunes and bogs to rocky hilltops and exposed outer-coast shorelines. In muskeg and sub alpine habitats, shore pine assumes a dwarf bonsai form, 1-2 m in height and often with a twisted trunk and branches. (Pojar and MacKinnon 1994). . Indian Plum (Osmoronia cerasiforms): It blooms early in the spring with green and white flower clusters; its light-green leaves begin to yellow in July. It has an open, arched branching pattern when in the open, and sprawling branches when in the shade. Indian plum can spread using underground suckers. Its orange, plum-like berries provide food for various birds and mammals and are somewhat edible to humans. Each plant is either male or female (Thurston County Conservation District). Dry to moist, open woods, streambanks, open areas (especially roadsides); low elevations (Pojar and MacKinnon 1994). . Willows are the most common trees used for stream revegetation. They are easily established from cuttings without added root hormone, and rapidly produce luxuriant growth. Willows have excellent soil-binding qualities and provide excellent browse for deer, elk, smaller mammals, and grouse. Willows often hang over the water, providing leaves and insects that drop from their branches and support the aquatic food chain. They also provide shade, which modulates summer water temperature. Most willows tolerate seasonal flooding. . Pacific Willow (Salix scouleriana): A small tree with one or more leaning, crooked trunks and an upright to rounded form. 20 to 40 ft tall deciduous shrub or tree; grows in coastal dune wetland communities along the outer coast and coastal freshwater swamps around Puget Sound. (Department of Ecology 1993). Tall, slender shrub or tree, to 12m tall; branches brown, twigs glossy, with yellow, duckbill-shaped buds, usually hairless, brittle at base; bark fissured yellowish-brown on older trees. Riverbanks, floodplains, lakeshores, and wet meadows; often standing in quiet, shallow river backwaters; sea levels to middle elevations (Pojar and MacKinnion 1994). . Hooker's Willow (Salix hookeriana): A sprawling shrub or cluster of trunks, with dense foliage and a rounded crown (Thurston County Conservation District). Wet places, often on the edge of standing water, sometimes on sandy beaches or dunes; low elevations (Pojar and MacKinnon 1994). 10 to 20 ft tall deciduous scrub or tree; grows in coastal dune wet land communities along the outer coast and coastal freshwater swamps around Puget Sound (Department of Ecology 1993). I I I I I I I I I I I I I LOG ITEM # ()-.co Pace (; of "'-0', - I I GeoEngineers File No. 10622-001-00 I e e I Port Ludlow Associates, Inc. July 24, 2003 Page 7 I I I I I I I I I I I I I I I I . Variable Willow (8. commutata): Spreading, much branched, 0.2 - 2 m tall; Riverside, wetland and high elevation thickets, lakeshores, gravelly benches, fresh alluvial and morainal materials, open forests. Late flowering. (Pojar and MacKinnon 1994). Black Twinberry (Lonicera lnvolucrata): 4 to 8 ft tall deciduous shrub; common along streams and in shrub swamps where soils are perennially moist; tolerates shallow flooding early in the growing season. (Department of Ecology 1993). Moist forest, clearings, streamside habitats, swamps and thickets; at low to subalpine elevations (Pojar and MacKinnon 1994). Salmonberry (R. spectabilis): 4 to 8 ft tall perennial shrub, spreads by rhizomes to form thickets in long streams and in forested swamps dominated by deciduous trees (Department of Ecology 1993). Moist to wet places (forests, disturbed sites), often abundant along stream edges, avalanche tracks and in wet logged areas; at low to subalpine elevations (Pojar and MacKinnon 1994). Wild Rose: The native rose plants have good soil-binding roots, and, once established, will spread by underground suckers to form thickets which provide excellent cover for birds and mammals. Nootka Rose (Rose nutkana): Has large, solitary, pink flowers that produce big purplish pear-shaped rosehips (Thurston County Conservation District). Spindly, to 3 m tall, with a pair of large prickles at the base of each leaf, other prickles usually absent except on some new growth. Grows in a variety of generally open habitats (shorelines, meadows, thickets, streamside areas, roadsides, clearings), at low to middle elevations (Pojar and MacKinnon 1994). Baldhip Rose (Rose gymnocarpa): Has clusters of small pink flowers, which produce brilliant orange or red rosehips (Thurston County Conservation District). Spindly, to 1.5 m tall, usually with numerous soft, straight prickles, sometimes unarmed especially on younger stems, which are usually covered with stalked glands (use hand lens). In a variety of habitats, from open to wooded, dry to moist; at low to middle elevations (Pojar and MacKinnon 1994). Skunk cabbage (Lysichiton americanum): 1 to 4 ft tall deciduous perennial herb; forms slowly expanding clumps by producing offshoots and can form monotypic stands in muck soils. A common component of forested swamps in western Washington, less common in east of the Cascade crest; typical associates include red alder, western red cedar, salmonberry, water parsley, and slough sedge (Department of Ecology 1993). Swamps, fens, muskeg, wet forest, mucky seepage areas, wet meadows; at low to middle elevations (Pojar and MacKinnon 1994). Slough sledge (c. obnupta): 1 to 3 ft tall, spreads by rhizomes to form monotypic stands; limited to western Washington. Tolerates deep shade or full sun and commonly grows in red alder-dominated swamps in association with skunk cabbage, water parsley, and salmonberry. Tolerates pH of 5.5 to 8.0 (Department of Ecology 1993). Marshes, LOG ITEM # 9-60 Page 7 . . . . . . . of I GeoEngineers File No. 10622-001-00 I e e I Port Ludlow Associates, Inc. July 24, 2003 Page 8 I I swamps, bogs, stream-banks, lakeshores, wet forest openings, meadows, clearings; common at low elevations (Pojar and MacKinnon 1994). . Sword fern (Polystichum munitum): to 1.5 m tall evergreen; grows in moist forests at low to middle elevations. (Pojar and MacKinnon 1994). . Salal (Gaultheria shaUon): A common plant, it is a robust, evergreen shrub which often forms dense thickets. It has lustrous, dark green leaves, showy pink flower clusters, and purplish-black berries that are eaten by birds, rodents, and people. Salal can be damaged by the strawberry root weevil (Thurston County Conservation District). Occurs in coniferous forests, rocky bluffs, to the seashore; low to medium elevations (Pojar and MacKinnon 1994). . Dune Grass (Elymus mollis): 0.5 - 1.5 m tall, forming large clumps with thick spreading rhizomes; stems stout, erect. Robust perennial. Coastal dunes, sand and gravel beaches, edges of shoreline forests; strictly maritime; often the dominant cover on offshore, treeless, sea-bird islands. (Pojar and MacKinnon 1994). . Salt Grass, Seashore Salt Grass (Distichlis spicata var. spicata): 10-40 cm tall, with solid stems and vigorous, scaly rhizomes. A sod-forming perennial. Tidal marshes, seashores; common at low elevations. (Pojar and MacKinnon 1994). . Douglas Aster (Aster subspicatus) 20-80 cm tall, perennial herb from a creeping rhizome or stembase; Beaches, meadows, streambanks, moist clearings; common at low to middle elevations throughout our region; typically a coastal species. (Pojar and MacKinnon 1994). I I I I I I I The impacted areas will be vegetated with native species that are perennials, have good soil- binding qualities, that grow relative quickly, and that provide habitat cover. Tables 1-4 specify the vegetative species, size, quantity, and spacing (on-center) of each species to be planted within the specific mitigation areas, Table 5 lists the total number of each species for all areas addressed in the planting plans. Figures A-2 through A-5 are conceptual maps of proposed species locations. I I I TABLE 1 NUMBER AND SPACING OF PROPOSED MITIGATION SPECIES FOR WETLAND AND WETLAND BUFFER AREA (FIGURE A-2) I Common Name Scientific Name Spacing Number to Plant Willow Salix commutata 6' o.C. 2110 Indian plum Oemleria cerasiformis 6' o.C. 1255 Slough sedge Carex obnupta l' o.C. 257 I I LOG ITEiVi # ~(() Page_o "...:: "'-I I I GeoEngineers File No. 10622-001-00 I e e I Port Ludlow Associates, Inc. July 24, 2003 Page 9 I I TABLE 1 (continued) NUMBER AND SPACING OF PROPOSED MITIGATION SPECIES FOR WETLAND AND WETLAND BUFFER AREA (FIGURE A-2) I Common Name Scientific Name Spacing Number to Plant Skunk cabbage Lysichiton americanum l' o.C. 257 Salal Gaultheria shallon 6' o.C. 855 Salmonberry Rubus spectabilis 6' o.C. 1426 Sword fern Polystichum munitum 12' o.C. 214 I I TABLE 2 NUMBER AND SPACING OF PROPOSED MITIGATION SPECIES FOR SHORELINE AREA NEAR TRACT B (FIGURE A-3) I Common Name Scientific Name Spacing Number to Plant Willow Salix hookeriana 6' o.C. 7841 Dune grass Elymus mollis l' o.C. 2628 Salt grass Distichlis spicata l' o.C. 1359 Twinberry Lonicera involucrata 6' o.C. 3404 Shore pine Pinus contorta var. contorta 12' o.c. 668 Nootka rose Rosa nootkana 6' o.C. 8482 Douglas fir Pseudotsuga menziesii 12' o.C. 668 I I I I TABLE 3 NUMBER AND SPACING OF PROPOSED MITIGATION SPECIES BEACH POINT I PICNIC AREA (FIGURE A-4) Common Name Scientific Name Spacing Number to Plant Willow Salix hookeriana 6' o.C. 765 Dune grass Elymus mollis l' o.C. 272 Salt grass Distichlis spicata l' o.C. 252 Twinberry Lonicera involucrata 6' o.C. 1009 Shore pine Pinus contorta var. contorta 12' o.C. 227 Nootka rose Rosa nootkana 6' o.c. 1067 Douglas aster Aster subspicatus l' o.C. 313 I I I I LOG ITEM # (}JX) Page q of I GeoEngineers File No. 10622-001-00 I I e e I Port Ludlow Associates, Inc. July 24, 2003 Page 10 I TABLE 4 NUMBER AND SPACING OF PROPOSED MITIGATION SPECIES FOR AREA I OF STREAM CROSSING (FIGURE A-5) Number to Common Name Scientific Name Spacing Plant Twinberry Lonicera involucrata 6' o.C. 396 Wild Rose Rosa gymnocarpa 6' o.C. 396 Douglas aster Aster subspicatus l' o.c. 99 Willow Salix hookeriana 6' o.C. 348 Salt grass Distichlis spicata l' o.C. 99 I I I TABLE 5 TOTAL NUMBER OF PROPOSED MITIGATION SPECIES FOR COMBINED AREAS I Number to Common Name Scientific Name Spacing Plant Douglas aster Aster subspicatus l' o.C. 412 Douglas fir Pseudotsuga menziesii 12' o.C. 668 Dune grass Elymus mollis l' o.C. 2900 Indian plum Oemleria cerasiformis 6' o.C. 1255 Nootka rose Rosa nootkana 6' o.C. 9550 Salal Gaultheria shallon 6' o.C. 855 Salmonberry Rubus spectabilis 6' o.C. 1426 Salt grass Distichlis spicata l' o.C. 1710 Shore pine Pinus contorta var. contorta 12' o.c. 895 Skunk cabbage Lysichiton americanum l' o.C. 257 Slough sedge Carex obnupta l' o.C. 257 Sword fern Polystichum munitum 12' o.C. 214 Twinberry Lonicera involucrata 6' o.C. 4809 Wild Rose Rosa gymnocarpa 6' o.C. 396 Willow Salix commutata 6' o.C. 11064 I I I I I I I I I I LOG ITEM #,$G () Page_@_of GeoEngineers FileNo. 10622-001-00 I I e e I Port Ludlow Associates, Inc. July 24, 2003 Page 11 I I Temporary erosion control Best Management Practices shall be implemented at all times during land disturbing activities. In efforts to control erosion and protect water quality, native vegetation in wetlands, streams, and their buffers, as well as in designated open space areas, shall be maintained in an undisturbed condition. Trees shall not be removed unless it is determined that a potential safety hazard exists. This Landscaping Plan has been prepared for the Ludlow Cove Residential Development proposed by Port Ludlow Associates, Inc. (PLA). Careful consideration was given to the points presented by Jefferson County as important in offsetting any significant adverse impacts on the environment. We have identified the extent of the proposed removal of invasive species and debris and topsoil in critical areas. The required wetland restoration, wetland buffer enhancement plan, and shoreline buffer area treatments have been described in detail. The plant species and assemblages were chosen based on site conditions and local plant communities. I I I I REFERENCES I The following documents were utilized in creating this report: . Pojar, Jim and Andy MacKinnon, et al. Plants of the Washington, Oregon, British Columbia and Alaska. 1994. Canada. . Thurston County Conservation District. Undated. A Guide to Stream Corridor Revegetation in Western Washington. Thurston County. . Washington State Department of Ecology. 1993. Restoring Wetlands in Washington: A Guidebook for Wetland Restoration, Planning and Implementation. Publication No. 93- 17, Olympia, Washington. Pacific Northwest Coast Lone Pine Publishing, I I I LIMITATIONS GeoEngineers has developed this planting plan in general accordance with the scope and limitations of our proposal. Within the limitations of scope, schedule and budget, our services have been executed in accordance with the generally accepted practices for Planting Plans in this area at the time this report was prepared. Activities and actions outside of Geoengineers control such as site design and construction by the contractor, plant stock origin/health, installation, irrigation and maintenance are very important aspects of success to this plan. Care should be taken to complete the planting as discussed and specified in this report to maximize the chance of success. No warranty or other conditions, express or implied, should be understood. This report has been prepared for the exclusive use of Port Ludlow Associates, Inc., their authorized agents and regulatory agencies following the described methods and information available at the time of the work. No other party may rely on the product of our services unless we agree in advance to such reliance in writing. The information contained herein should not be applied for any purpose or project except the one originally contemplated. I I I I I I LOG ITEM '~B:t)() Pag~~",.LI~or GeoEngineers File No. 10622-001-00 I I e e I Port Ludlow Associates, Inc. July 24, 2003 Page 12 I I Any alteration, deletion or editing of this document without explicit written permission from GeoEngineers, Inc. is strictly prohibited and may jeopardize the success of the plans. Any other unauthorized use of this document is prohibited. This document is intended to be used in its entirety. If an excerpt is quoted or paraphrased, it must be properly referenced. Any electronic form, facsimile or hard copy of the original document (email, text, table, and/or figure), if provided, and any attachments are only a copy of the original document. The original document is stored by GeoEngineers, Inc. and will serve as the official document of record. I I I ~ -} ~ I I I I I I I I I I LOG ITEM .,. 'dD () P~ge~ '{ ):.- -'of , ---... I GeoEngineers File No. 10622-001-00 I I e e I Port Ludlow Associates, Inc. July 24, 2003 Page 13 I I We appreciate the opportunity to be of service to you on this project. Please contact us if you have questions, or require clarification regarding the information presented in this report. If you have any questions feel free to contact me at (360) 769-8400. Respectfully submitted, I GeoEngineers, Inc. I lwp f). ]?.e",~ Lisa Berntsen, PWS Principal I I JWP:LAB:j1 ORCH\1 0\ 1 0622001 \OO\Finals\ I 062200 1 OOR.doc. I Disclaimer: Any electronic fonn, facsimile or hard copy of the original document (email, text, table, and/or figure), if provided, and any attachments are only a copy of the original document. The original document is stored by GeoEngineers, Inc. and will serve as the official document of record. I Enclosures: Figure 1 - Shematic of Footbridge Appendix A - Conceptual Planting Plans Figure A-I - Figure Locations Figure A-2 -Wetland and Buffer Areas Figure A-3 - Shoreline Area Figure A-4 - Beach Point Picnic Area Figure A-5 - Area of Stream Crossing I I cc: Jerry Smith Jefferson County Planning Department 621 Sheridan St. Port Townsend, W A 98368 I I I I I LOG 'TEM # 7)J)1) Pag€_}~_o'f_~ I GeoEngineers File No. 10622-001-00 I I I ~:" I I I "'..... , I "3' ~. ..~ trZ o "".~ ~;~ <' ~ Z, ,~ ~O ~.~ .~ Z ~ n~,~ ~ I"IL:. ~~~~ 'Q~ ,~. i;1Z~ ~Z ~r, ~~.~ I I I I I I I ~ lili I I "'" ': 15 t':~ I ~ I I I e e ii'" 1'i v ~ "~, \!' j [f .~ t~ ~ 1.,1 ". '\:i I ~H .~ ,\:, ~ i" '!, ~ . '" ;-.., :1; ...., m 'r ,. if~ .'!i E:_:~ l~ ~ ":"'~ ~;r, l;r j ~~' -- j 1 I ! l< I, ~ " '<'" -----) ---" '.- -- -- , "- " " ,,-, , , '~ L ;t:t ~ It.. '1 ~ ...:l < U rJ1 o :Z C W Z z ii: C) z ~ =>z ....0 <C- W.... LL<C wC C)Z => ,CO ~LL alC) ....Z 0- O:::! LLD.. 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