habitat installed in marsh creek state park

Download Habitat installed in marsh creek state park

If you can't read please download the document

Upload: james-wassell

Post on 04-Aug-2015

1.263 views

Category:

Documents


0 download

TRANSCRIPT

1. The people have a right to clean air, pure water,and to the preservation of the natural, scenic, historic and esthetic values of the environment. Pennsylvanias public natural resources are thecommon property of all the people, including generations yet to come. As trustee of theseresources, the Commonwealth shall conserve andmaintain them for the benefit of all the people. 2. Notice:Marsh Creek Lake DrawdownMarsh Creek State Park is planning an 8 foot drawdown of thelake for a large scale fish habitat project.The drawdown is expected to be complete by October 15, 2012 with the intent to return the lake to normal pool by earlyMarch 2013.During this time, docks may be impacted. Boating will bepermitted; however, boating access could be limited.A public meeting will be held to discuss this project on Thursday September 6th 2012 6:00 pm in the cafeteria at Pickering Valley Elementary School.Please call park office for more information 610-458-5119 3. Volunteer scale project MarshCreek Bass club 4. Shoreline trees 5. Post clusters 6. Draw down 2013, 8 feet 7. The 2013 crew fishcommission and DCNR 8. Spider humps 9. Before 10. Before 11. Before 12. Before 13. Before 14. After 15. After 16. After 17. After 18. After 19. After 20. After 21. Rock Stars 22. Before 23. After 24. After 25. Dont let the parkmanager drive an ATV 26. Working on docks 27. Black Bass Nesting StructureBlack Bass Nesting Structures are a spawning/nesting/nursery-type habitat, designed to accommodate thespawning/nesting/nursery habits of black bass (largemouth and smallmouth). Bass Nesting Structures aredesigned to provide maximum shallow-water (less than 10 feet) cover to adult bass, during the pre- and post-spawn periods, and dense refuge cover for young-of-the-year smallmouth and largemouth bass. Classic nativespawning habitats for black bass occur along south-facing shores in bays and inlets, but spawning may occur atmain lakeshores, too. Native spawning sites treated with overhead cover appear to enhance adult spawningand nesting activities, plus improve young-of-the-year survival. Normally, five to 10 nesting structures areplaced at one site. Bass Nesting Structures are usually placed in alternating rows, in depths between five and 10feet, depending on water clarity and the target species. The Bass Nesting Structure is only 15 inches high, soeven at five-foot depths, it is not a navigation hazard. The exception would be during drawdown periods,when the structure could become exposed. Typical placement density is 10 structures per acre.Turtle Basking PlatformsSince the Pennsylvania Fish & Boat Commission is responsible for the protection and management of turtles inthe Commonwealth, the Habitat Management Section has designed an artificial turtle basking habitat,.Pennsylvania Turtle Basking Habitat Platforms were originally designed for red-bellied turtles at LakeMarburg, York County, due to a sighting of these rare animals. During the initial evaluation of the baskinghabitat structures at Lake Marburg, it was realized that the platforms were utilized by a variety of turtles, not just the Pennsylvania-threatenedred-bellied. Other turtle species could benefit from the placement of artificial basking habitats. ManyPennsylvania reservoirs contain little, if any, woody debris appropriate for turtles to use as basking habitat.This is primarily due to pre-impoundment reservoir clearing and continued debris removal. Withoutappropriate basking habitat, many turtle species are not able to properly adjust body temperature. Baskingprovides opportunities for resting and allows turtles to increase their body temperature, which promotesindividual growth, aids digestion, reduces susceptibility to disease and improves overall health. The sitesselected for basking platforms are normally places where turtles have already been seen and where thestructure will receive little attention from humans, during soft-water periods. These sites are generally in baysand coves in the upstream areas of impoundments. The Pennsylvania Turtle Basking Platform is a modifiedversion of the original Codorus design. The modification makes the platform less complicated to construct andprovides increased escape possibilities. Typical placement density is five structures per acre. 28. Post ClustersMost Pennsylvania-style artificial wood habitat structures are designed on a horizontal coverprinciple. Post Clusters are designed to create long-lasting, functional, vertical, shallow-watercover for game and panfish. Designed primarily for flatland and hill-land impoundments, PostClusters utilize common agricultural fence posts, driven into the impoundments substrate in acluster pattern, to create shallow-water, vertical ambush cover for black bass. Post Clustersalso create simple microhabitat for aquatic invertebrates. These microhabitats may also serveas habitat for prey resources of black bass (and other predators), increasing prey/predatorefficiency. Simple vertical habitat also provides camouflage-related benefits to game andpanfish. Pennsylvania Post Clusters are typically placed in three to four-foot depths, at slightangles to the water surface. Placement is accomplished during seasonal or maintenancedrawdown periods, by specialized construction or agricultural type equipment, with ahydraulic fence post driver. Typically, 8 x 6 posts are driven into the substrate,approximately three to three-and-a-half feet, allowing12 to 18 inches of the post to be above the water surface in three to four-foot depths. PostClusters are placed six to eight feet apart, with 25 posts to a cluster. Typical placement densityis four (25-post) clusters per acre.Felled Shoreline TreeWhere sufficient depths exist near shore (greater than 15 feet), felling and cabling shorelinetrees provides excellent fish habitat. Game and panfish use submerged trees in a variety ofways. Spawning, recruitment, foraging and refuge tasks are accomplished by many speciesand age-classes using felled trees. Large, spreading hardwood trees are particularly suitable,because their complex branching systems create more complex habitat. Trees are felled andcabled to their stumps (see standard drawing), with -inch galvanized wire rope and cableclamps. Typical placement density is five trees per acre. 29. Porcupine CribsPorcupine Cribs are long-lasting, deep-water, complexstructures designed as a refuge-type habitat. This design should provide protection for juvenile fishand improve recruitment of pan fish and game fish in impoundments that lack abundant, deep-water, submerged aquatic vegetation.Placement is traditionally accomplished by specially-equipped watercraft, during soft-waterperiods (no ice). These structures may also be constructed on-site, during drawdown periods.Submerged structures are normally placed in a row or alternating row pattern, with four to eight-foot spaces between individual structures. Normally, 10 to 20 Porcupine Cribs are placed at onesite. Structures are submerged in 10 to 15-foot depths along the bottom contour, parallel to theshore. Typical placement density is 20 structures per acre. Typically, native habitats in hill-landimpoundments (see page 39) benefit most from coarse brush structures. High-gradient slopes,leading into breaks and/or channels, characterize these areas. Steep shores that break onto flats orbenches appear to be effective native habitats, when treated with coarse-brush-type artificialstructures.Porcupine Crib Jr.The Porcupine Crib Jr. is an adaptation of the original Porcupine Crib,which was designed as a deep-water structure. The Jr. is a shallow-water version, withadditional density in the gable ends. The Porcupine Crib Jr. was first designed to mimic the habitatprovided by native stumps. Stumps in shallow water provide an important habitat value inPennsylvania reservoirs and are sometimes the only true woody cover in an impoundment. Asimpoundments age, native stump fields may disappear, due to erosion by wind or by annual orseasonal maintenance drawdowns. As the stump fields disappear, so does that type of cover. Someimpoundments do not contain any native stumps, as a result of policies in place duringimpoundment construction. Porcupine Crib Jrs. can provide alternative cover for pre- and post-spawning adult pan fish and black bass, plus seasonal ambush and refuge cover for juveniles. 30. Spider Humps and Rock StarsSpider hump and rock star structures provide similar habitat features asrock rubble humps but with the addition of wooden posts and boardscreates a more complex habitat structure that may attract more diversity infish species. Spider hump structures may also provide foraging and ambushcover for walleye, black bass, and pan fish. Fish use depends on location,placement, density, and depth. Traditional site for placement is shallowflats, slow tapered shores or shawls in flatland or hill land impoundments.Spider humps are placed in a sinuous pattern, parallel to the shoreline. Thismethod has been documented as a successful warm water fish habitatplacement pattern. Construction and placement is accomplished with heavymachinery, typical placement density is five spider hump structures peracreThese two types of structures were installed during the winter of 2013.These structures require large equipment to install. The lake was dropped 8feet in November of 2012. This is the most the lake was ever dropped sinceit was filled in 1974.The rest of these artificial habitats have been installed over many years withthe cooperation of volunteers the Department of Conservation and NaturalResource and the PA Fish and Boat commission