DCNR State Forest Resource Management Plan

State Forest Resource Management Plan
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WATER RESOURCES

 

Table of Contents

Introduction
History
Water Resources Inventory
  Rivers and Streams
  Lakes and Ponds
  Watersheds
  Groundwater
  Impaired Water Bodies
  Palustrine and Wetland Communities
  Spring Seeps and Vernal Ponds
  Aquatic Community Classification
Policy Statement
Goals and Objectives
Guidelines and Actions
  Environmental Reviews
  General Guidelines for Managing Water Resources
  Zoning Guidelines for Considering Water Resources
  Guidelines for Managing Municipal Watersheds
  Guidelines for Special Protection Waters
  Guidelines for Protecting Spring Seeps and Vernal Ponds
  Guidelines for Activities in Wetlands, Aquatic Ecosystems, and Riparian Ecosystems
  Guidelines for Groundwater Conservation and Protection
  Guidelines for Coordinating Water Resources Management with Other Management Considerations
  Actions for Goals and Objectives
Monitoring
Critical Research Needs

 

Introduction

In the context of forest resource management, the Bureau of Forestry views “Water Resources Management” as an array of potential resources, impacts, issues, and opportunities encompassing all water resources, values, uses, and functions. Water resources include watersheds, riparian ecosystems, aquatic ecosystems (surface waters), groundwater systems, and social values and uses of water resources such as for drinking, recreation, aesthetic enjoyment, research and industrial uses. This scope and complexity demonstrates the need for managing water resources within the broader context of forest ecosystem management.

Drinking Water

On state forest lands near populated areas, the demand for potable water is increasing and beginning to approach the limit of available supplies from impoundments and reservoirs. Remote areas of state forest lands will continue to serve as a reserve of clean water. In addition to providing water from surface sources, state forest lands also provide access to potable groundwater and serve as significant groundwater recharge areas. A number of rural municipalities have entered into agreements with the Bureau of Forestry to drill municipal water wells on state forest lands. Public ownership, scientific-based management, and the vast geographic extent of state forest lands make them uniquely suited to continue to provide clean water for Pennsylvanians. The Bureau of Forestry will cooperate with agencies such as the US Geologic Survey and DCNR, Bureau of Topographic and Geologic Survey to protect surface and groundwater resources.

"In-stream" Values-Ecological Functions, Aquatic Ecosystems, and Recreation

Water for municipal and household uses might be the most obvious and valuable benefit to the Commonwealth, but water also has intrinsic "in-stream" values and functions such as recreation, aesthetics, and habitat for aquatic life. Additionally, wetlands and riparian zones act as natural filters of sediment and pollutants, and clean water from forested watersheds helps to dilute pollutants entering the system. Forested watersheds and riparian zones greatly influence the ability of surface waters to provide in-stream values, uses and functions; and thus, will be managed as integral components of forest ecosystems.

There are many different kinds of aquatic ecosystems on state forest lands, the majority of which are moving-water systems (rivers, streams) or lakes and/or ponds. The nature and quality of these systems are critical to the survival of thousands of fauna species on State Forest lands.

Riparian areas, or streamside forests are critical to the protection of aquatic ecosystems. Due of their location, riparian areas play a critical role in protecting water quality, reducing soil erosion, and enhancing fish and wildlife resources. Also, because of the dendritic pattern exhibited by most of the streams on state forest land, riparian zones provide travel lanes or corridors for many wildlife species. Aquatic and riparian system are linked. Riparian habitats form a natural buffer between an aquatic ecosystem and the drier upland terrestrial systems.

Recreational expectations of state forest lakes, ponds, and streams vary among users. Some use water resources for environmental education, while others may use it for fishing, boating, hunting, or trapping. Still others simply wish to observe the plants and animals associated with aquatic ecosystems. Water-related recreational interests are extensive and often times conflict, which means that not every water body can simultaneously support all activities. Therefore, in areas of high recreation use, the Bureau of Forestry will base recreation management decisions on designated primary uses of each water body in an attempt to minimize conflict among recreation users, while also protecting the ecological values of the resource.

Aquatic Community Classification

An aquatic community classification project is currently underway in Pennsylvania by the Natural Heritage program including The Nature Conservancy, the Western Pennsylvania Conservancy and the Department of Conservation and Natural Resources, Bureau of Forestry. The Pennsylvania Aquatic Community Classification Project (project) proposes to develop and apply standardized aquatic ecosystem classifications and reference conditions, which will allow conservation planners to identify, characterize and map existing locations of freshwater plants and animals and their habitats across the state and assess their relative conservation priority. The project will help identify the highest priority areas for aquatic resource protection as well as augment and strengthen statewide conservation programs while providing important data to watershed groups and other organizations in order to assist local watershed planning, protection and restoration efforts. For more information on the project refer to the Fauna Resources section of this plan.

Management Practices

The Bureau of Forestry will continue to develop and implement best management practices (BMPs) to minimize and prevent water pollution, as well as support and engage in research to restore degraded surface and groundwater resources. Erosion and sedimentation, acid mine drainage, acid precipitation, and chemical and thermal pollution are notable examples of human-caused factors adversely affecting water resources. Controlling inputs into aquatic systems, both negative and positive, (e.g., limestone to increase the buffering capacity of acidic streams is beneficial) is essential for maintaining and improving the quality of Pennsylvania's water resources.

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History

The Commonwealth of Pennsylvania began protecting watersheds in 1897 when the legislature passed an act authorizing the purchase of unseated lands for forest reservations in the headwaters of each of the main rivers of the Commonwealth, including the Delaware, Susquehanna, and Ohio Rivers. This foresight, along with subsequent legislation, helped to acquire and establish the present state forest system, which today serves as a 2.1 million-acre source of clean water for Pennsylvania. One of the original purposes for establishing the state forest system was to protect forested watersheds, and this remains part of the Bureau of Forestry's mission today.

Historically, the Bureau of Forestry's water resources management and planning efforts focused on protecting watersheds to maximize the supply and production of potable water, as well as protecting and improving wetland and aquatic habitats. This is evidenced by the former name given to the Bureau of Forestry, "The Department of Forests and Waters."

The management objectives of the first "official" management plan, the Forest Resource Plan of 1955-1970, were to:

  1. Produce the greatest possible sustained supply of timber products.
  2. Improve species composition and quality of existing stands and provide for adequate residual growing stock as well as reduce the damage caused by insects and diseases.
  3. Regulate the cutting of timber so that the supply and flow of products from the forest will be constant and adequate. This will tend to stabilize wood-using industries and the employees and communities dependent upon them.
  4. Develop and preserve the recreational values of the forests.
  5. Protect the watersheds from erosion and obtain from them the maximum yields of useable water.
  6. Harvest timber in such a way that an adequate, uniform supply of food and cover for wildlife is produced.

Objective number five clearly states the bureau's intentions of protecting watersheds and providing clean water. The subsequent Forest Resource Plan (1970-1984) included a "Watershed Management Section" with specific objectives for watershed management:

To make available the maximum yield of potable water under sound multiple-use practices by:

  1. Restricting or limiting activities and development on watersheds to practices that will neither reduce the quantity nor impair the quality of the water.
  2. Analyzing future water needs of communities within or near state forest lands and designating potential watersheds that can be developed to fill those needs.
  3. Zoning to control future development on watersheds in order to protect the water resources.

Objectives one and two of the "Watershed Management Section" of the 1985-1999 State Forest Resource Plan were very similar to the 1970-1984 Plan. Objective number three of the 1985-1999 Plan was added to address the notion of coordinating management activities.

  1. To restrict or limit present and future activities and development on watersheds to practices that will neither reduce the quantity nor impair the quality of the water.
  2. To review future water needs of communities within or near state forest lands and designate potential watersheds that can be developed to fill those needs.
  3. To coordinate the use and development of water resources so as to protect and enhance water quality and the other forest resources.

As the Bureau of Forestry develops and implements the 2000-2005 State Forest Resource Management Plan, it will expand its water resources management efforts to consider all water resources, uses, values, and functions within the broader context of forest ecosystem management.

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Water Resources Inventory

The Water Resources Inventory contains information on the following resources:

  • Rivers and Streams
  • Lakes and Ponds
  • Watersheds
  • Groundwater
  • Impaired Water Bodies
  • Palustrine and Wetland Communities
  • Spring Seeps and Vernal Ponds
  • Aquatic Community Classification

Rivers and Streams Inventory

In Pennsylvania, the Department of Environmental Protection (DEP), the Pennsylvania Fish and Boat Commission (PA FBC), and the Department of Conservation and Natural Resources, Bureau of Recreation and Conservation (DCNR, R&C) are the primary agencies responsible for determining special protection designations for rivers and streams.

A. DEP Special Protection Waters

Under Title 25, Pennsylvania Code, Chapter 93. Water Quality Standards, all waters within the Commonwealth have been classified according to present condition and use. Waters receiving special protection include High Quality Waters (HQ) and Exceptional Value Waters (EV). HQ and EV waters are defined as follows:

HQ: "A stream or watershed which has excellent quality waters and environmental or other features that require special water quality protection."

EV: "A stream or watershed which constitutes an outstanding national, state, regional or local resource, such as waters of national, state or county parks or forests, or waters which are used as a source of unfiltered potable water supply, or waters of wildlife refuges or State game lands, or waters which have been characterized by the Fish Commission as 'Wilderness Trout Streams,' and other waters of substantial recreational or ecological significance."

The following links provide access to DEP websites containing information on water quality standards and stream designations:

2002 Section 305(b) - Water Quality Assessment Report
Past Section 305(b) Reports - for historical reference: 2001 || 2000 || 1998 || 1996

Statewide Existing Use Classifications

Stream Redesignation Evaluations - Status and Draft Reports

Pennsylvania's Surface Waters Assessment Program - 2002 Update

In cooperation with DEP, the Bureau of Forestry compiled a listing of the special protection waters (EV and HQ) on state forest land organized by state forest and county. There are approximately 2,970 miles of HQ and 626 miles of EV waters on state forest land. A table at the end of this section provides a listing by state forest. For example, below is a listing of stream designations for Adams County in the Michaux State Forest. The listings for remaining counties and state forests can be found in the following file: State forest waters with special protection list (Adobe PDF 163 Kb). Additionally, the Bureau of Forestry maintains GIS layers of rivers and streams and their corresponding designations.

Special Protection Waters of Michaux State Forest

ADAMS COUNTY STREAM NAME BASIN REACH DESIGNATION
Birch Run Conococheague Creek Basin, (Cumberland & Adams Counties) HQ-CWF
Carbaugh Run Conococheague Creek Basin, source to first pipeline crossinupstream of Route 30 (Adams & Franklin Counties) EV
Carbaugh Run Conococheague Creek Basin, Pipeline crossing upstream of Route 30 to Adams/Franklin County line HQ-CWF
East Branch Antietam Creek Antietam Creek Basin, source to Adams/Franklin County line HQ-CWF
Hosack Run Conococheague Creek Basin (Adams & Franklin Counties) HQ-CWF
Middle Creek Toms Creek Basin, source to Route 116 Bridge at Fairfield HQ-CWF
Mountain Creek Yellow Breeches Creek Basin, source to Adams/Cumberland County line HQ-CWF
Stillhouse Run Conococheague Creek Basin HQ-CWF
Toms Creek Monocacy River Basin, Adams/Franklin County line to LR 01053 Bridge HQ-CWF
(West) Conewago Creek Susquehanna River Basin, source to Pleasant Dale Creek HQ-CWF

Current through 30 PaB 6191 on December 2, 2000 (Trout Run)

B. PA FBC-Trout Stream Designations

1. Pennsylvania Class A Wild Trout Streams

Definition - Streams that support a population of naturally produced trout of sufficient size and abundance to support a long-term and rewarding sport fishery.

Management - Natural reproduction of wild populations without stocking. The following file, maintained by the PA FBC, contains a listing of naturally reproducing trout streams on state forest land.

2. Pennsylvania Wilderness Trout Waters Definition:

Wilderness trout stream management is based upon the provision of a wild trout fishing experience in a remote, natural and unspoiled environment where man's disruptive activities are minimized. Established in 1969, this option was designed to protect and promote native (brook trout) fisheries, the ecological requirements necessary for natural reproduction of trout and wilderness aesthetics. The superior quality of these watersheds is considered an important part of the overall angling experience on wilderness trout streams. Therefore, all stream sections included in this program qualify for the Exceptional Value (EV) special protected water use classification, which represents the highest protection status provided by the Department of Environmental Protection (DEP).

The PA Fish and Boat Commission maintains a listing of Class A Wild Trout Streams and Wilderness Trout Waters on their website: http://sites.state.pa.us/PA_Exec/Fish_Boat/pfbchom2.html

3. The following file contains a listing of PA FBC waters on state forest land by grouped by Pennsylvania county: State Forest Water Pa Fish & Boat CommWaters (Adobe PDF 35 Kb).

C. DCNR, R&C Scenic Rivers Program

PA Scenic Rivers logo

For purposes of designating and managing rivers for recreation and aesthetic enjoyment, the DCNR, Bureau of Recreation and Conservation developed the Pennsylvania Scenic Rivers Program. The link below provides access to the Bureau of Recreation and Conservation's Rivers Program:

http://www.dcnr.state.pa.us/brc/rivers/index.htm

Classification Criteria

Rivers included in the Scenic Rivers System will be classified, designated and administered as Wild, Scenic, Pastoral, Recreational and Modified Recreational Rivers (Sections 4; (a) (1) of the Pennsylvania Scenic Rivers Act). A designated river may have more than one classification; each segment will have its own classification, and must be long enough to provide a meaningful experience. The number of different classified segments within the river should be kept to a minimum.

WILD or SCENIC river designations are intended to preserve the primitive qualities the natural, and aesthetic values of a river and also to protect the existing character and quality of both the river and its adjacent land environment.

Wild rivers shall be free flowing and supportive of native fish and wildlife. The shorelines and adjacent environment shall be pristine in character. Access to segments is restricted to foot and/or nonpowered watercraft.

Scenic rivers shall be free flowing and capable of, or under restoration, to support water-cased recreation, fish and aquatic life. The view from the river or its banks shall be predominately wild, but may reveal some pastoral countryside. The segment may be intermittently accessible by road.

PASTORAL river designation is intended to recognize the capability and productivity of agricultural activities. The surrounding pastoral landscape enhances the aesthetic qualities of this river type.

Pastoral rivers shall be free flowing excepting historic or restored mill dams and capable of, or under restoration, to support water based recreation, fish and aquatic life. The view from the river or its banks shall be predominately pastoral of farming countryside. The segment may be intermittently accessible by roads.

RECREATIONAL and MODIFIED RECREATIONAL designations are intended to maintain the utilization of the river and its adjacent land environment for recreational uses. Such use however, must be compatible with the capability of the resource to support that use without degradation.

Recreational rivers may combine free flowing and relatively short stretches of impounded water that can, or is being restored to, sustain appropriate water-based recreation, fish and aquatic life. The shorelines may exhibit considerable man-made modification; however, such modification shall be compatible with the aesthetics of the river environment. The river shall be readily accessible.

Location Map

The map below shows the location of Pennsylvania designated Scenic Rivers. Federally designated Scenic Rivers are not depicted in this map. The colored corridors represented in and around the map are linked to more detailed maps that better locate the boundaries of each river, and include river segments and their designated uses.

Map of PA showing Scenic Rivers

Pennsylvania Scenic Rivers on state forest land include:

Yellow Breeches Creek (Michaux State Forest)
Pine Creek (Tioga State Forest)
Lick Run (Sproul State Forest)
Schuylkill River (Weiser State Forest)
Octorora Creek (Valley Forge State Forest)

The table below summarizes stream and river designations on state forest lands. For maps and additional information please refer to one of the 20 specific State Forest Resource Management Plans.

Pennsylvania
Federal
  Name Date designated   Name Date designated
1 LeTort Spring Run
March 1988 1 Middle Delaware River September 1965
2 Yellow Breeches Creek December 1992 2 Upper Delaware River November 1978
3 Stony Creek March 1980 3 Allegheny River April 1992
4 Pine Creek December 1992 4 Clarion River October 1996
5 Lehigh River April 1982 5 White Clay Creek October 2000
6 Lick Run December 1982 6 Lower Delaware River November 2000
7 French Creek April 1982      
8 Schuylkill River November 1978      
9 Tulpehocken Creek December 1992      
10 Lower Brandywine June 1989      
11 Octoraro Creek October 1983      
12 Tucquan Creek December 1988      
13 Bear Run December 1988      

 

The table below summarizes stream and river designations on state forest lands. For maps and additional information please refer to one of the 20 specific State Forest Resource Management Plans.

Miles of rivers and streams on state forest lands.
State Forest Total EV HQ PC WT WW SR
Michaux 202 0 178 0 11 0 0
Buchanan 162 19 115 12 0 12 0
Tuscarora 174 0 132 10 13 2 0
Forbes 184 40 61 39 4 0 0
Rothrock 185 0 192 0 0 0 0
Gallitzin 42 0 15 18 0 11 0
Bald Eagle 393 23 247 39 0 0 0
Clear Creek 58 2 33 4 0 0 0
Moshannon 505 17 253 109 23 0 0
Sproul 731 103 371 115 0 54 12
Lackawanna 17 0 0 12 5 0 0
Tiadaghton 451 46 357 0 0 0 0
Elk 536 65 316 112 0 0 0
Cornplanter 4 0 0 5 0 0 0
Susquehannock 802 199 394 8 119 0 0
Tioga 394 92 95 165 25 7 16
Valley Forge 2 0 0 1 0 0 6
Weiser 16 0 0 0 0 0 0
Delaware 163 6 148 0 0 0 2
Wyoming 113 13 65 26 7 0 0
Totals 5,132 * 626 2,970 675 207 86 36

* This total includes all streams in the Bureau of Forestry's GIS database, not all of which were designated into one of the categories listed.

EV = Exceptional Value Waters (DEP)
HQ = High Quality Waters (DEP)
PC = Perennial Cold Water Streams (PA BOF)
WT = Wilderness Trout Streams (PA FBC)
WW = Warm Water Streams (PA FBC)
SR = Scenic River (DCNR, R&C)

 

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Lakes and Ponds Inventory

Natural and Human-made impoundments,
lakes and ponds on State Forest Land.
State Forest Acres of Natural Lakes and Ponds Acres of Human-made Impoundments
Michaux 0 232
Buchanan 0 0
Tuscarora 0 0.5
Forbes 0 6
Rothrock 0 18
Gallitzin 0 32
Bald Eagle 0 0
Clear Creek 0 0
Moshannon 29 69
Sproul 2 14
Lackawanna 0 0
Tiadaghton 13 3
Elk 16 0
Cornplanter 0 0
Susquehannock 0 0
Tioga 48 8
Valley Forge 0 0
Weiser 0 0
Delaware 192 474
Wyoming 0 57
Totals 300 913.5

 

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Watershed Inventory

As part of the Pennsylvania State Water Plan, DEP delineated 104 watersheds in Pennsylvania's six major river basins. The map below shows the major river basins and the link provides access to DEP's Watershed Notebooks website, which provides additional information on each watershed.

Pennsylvania's Major Watersheds

http://www.dep.state.pa.us/dep/deputate/watermgt/WC/Subjects/WSNoteBks/shedtable.htm

Graphic of PA showing major watersheds

The Bureau of Forestry GIS Library contains GIS data for the State Water Plan watersheds. Bureau of Forestry personnel can use these data to consider the watershed impacts of policy and management decisions.

First delineated as part of the 1970-1984 Forest Resource Plan, and updated since, the table below lists the acres of state forest land designated as municipal watersheds, along with potential watershed acres.

Existing and Potential Municipal Watersheds
and Streams on State Forest Land
State Forest Total acres Acres of Existing
Municipal Watersheds
Acres of Potential
Municipal Watersheds
Michaux 85,008 21,787 25,213
Buchanan 70,244 6,560 0
Tuscarora 91,026 19,637 0
Forbes 51,435 2,034 7,505
Rothrock 94,264 7,108 7,287
Gallitzin 15,337 6,695 0
Bald Eagle 196,213 67,450 23,847
Clear Creek 13,299 2,000 0
Moshannon 185,885 21,698 9,197
Sproul 292,000 19,744 52,464
Lackawanna 8,431 1,100 0
Tiadaghton 213,883 10,852 0
Elk 197,729 11,695 5,000
Cornplanter 1,487 0 0
Susquehannock 261,807 5,097 0
Tioga 162,311 1,370 33,527
Valley Forge 912 0 0
Weiser 19,361 6,540 0
Delaware 82,000 3,680 685
Wyoming 43,580 0 0
Totals 2,086,212 215,057 164,725

 

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Groundwater Inventory

Groundwater Sources of Information

The Internet provides access to a wealth of information on groundwater resources in Pennsylvania:

  1. The PA DCNR, Bureau of Topographic and Geologic Survey provides background information on the geology of Pennsylvania's groundwater, water well information, along with links to other data, information, agencies, and organizations devoted to groundwater protection and management.

    http://www.dcnr.state.pa.us/topogeo/groundwater/groundwater.htm

    Pennsylvania Ground Water Information System

    The Pennsylvania Topographic and Geologic Survey (PaGS) developed and maintains a groundwater database for Pennsylvania called the Pennsylvania Groundwater Information System (PaGWIS). This MS Access database contains information on construction, location, and hydrogeologic data for water wells; improvement and hydrogeologic data for springs; and water quality information for selected wells and springs. These data were gathered from databases of the PaGS, the United States Geologic Survey, the PA Department of Environmental Protection, and the PA Department of Agriculture. In addition to the Access database, the PaGS developed GIS coverages representing the ground water sites, which allows users to visually ascertain what information is available for specific areas of Pennsylvania.

    From the PaGWIS database, the PaGS developed another database titled, "Hydrogeologic Characteristics of the Stratigraphic Units on the 1980 State Geologic Map in the Ridge and Valley Physiographic Province, Pennsylvania." This database provides a regional statistical summary of the hydrologic, water chemistry, and well construction characteristics of the stratigraphic units on PaGS's 1980 edition of the state geologic map. The PaGS is planning to expand this database to the remainder of Pennsylvania.

    The Bureau of Forestry plans to use this ground water information when planning management activities on state forest land having the potential to affect ground and surface water resources. Additionally, these data could help to identify new sources of potable water as demand increases in the future.

    The table below shows that there are currently 126 groundwater wells and 17 surface water intakes on state forest land. Intakes for inholdings adjacent to state forest lands are also shown, since they are most likely affecting the water resources on state forest, and vice versa. Maps such as the one below have been developed for each state forest
Public Surface and Groundwater Intakes on State Forest Land
and Inholdings Adjacent to State Forest Land.
State Forest Surface
Intake
Surface Intake on
Adjacent Inholding
Groundwate
Intake
Groundwater Intake
on Adjacent Inholding
Michaux 7 1 8 6
Buchanan 0 0 6 2
Tuscarora 1 0 2 2
Forbes 0 0 7 18
Rothrock 2 0 7 7
Gallitzin 0 0 1 0
Bald Eagle 1 2 12 8
Clear Creek 0 0 1 0
Moshannon 0 0 3 4
Sproul 2 2 4 6
Lackawanna 0 0 2 0
Tiadaghton 2 0 6 3
Elk 1 0 4 2
Cornplanter 0 0 1 0
Susquehannock 0 0 11 13
Tioga 1 0 16 0
Valley Forge 0 0 0 0
Weiser 0 0 5 0
Delaware 0 0 17 17
Wyoming 0 0 13 2
Totals 17 5 126 90

Map showing water wells and surface-water intakes within the Michaux State Forest

2.

The PA DEP, Bureau of Watershed Management provides guidelines for protecting groundwater resources as well as information regarding water well regulations and permits.

http://www.dep.state.pa.us/dep/deputate/watermgt/wc/subjects/srceprot/default.htm#gw_protect

http://www.dep.state.pa.us/dep/deputate/watermgt/watermgt.htm

 

3. The United States Geologic Survey (USGS) provides online real-time and historic groundwater information on streams and water wells across Pennsylvania.

http://pa.water.usgs.gov/

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Impaired Water Bodies Inventory

The Department of Environmental Protection (DEP) has an ongoing program to assess the quality of waters in Pennsylvania, according to Section 303(d) of the Federal Clean Water Act. Water quality standards are comprised of the uses that the waters can support and the goals established to protect those uses. Uses include, among other things, aquatic life, recreation, and drinking water, while the goals are numerical or narrative water quality criteria that express the in-stream levels of substances that must be achieved to support the uses. Periodic reports on the quality of waters in the Commonwealth are required under section 305(b) of the federal Clean Water Act.

The link below is to DEP's website for impaired water bodies, which are listed and organized according to the State Water Plan.

Final 2002 Section 303(d) Report - List of Impaired Waterbodies
Past Section 303(d) Report - for historical reference: 1998

Related to the above-referenced information available through DEP, the U.S. EPA maintains a website for impaired waterbodies, searchable by state:

http://oaspub.epa.gov/waters/region_rept.control?p_region=3#IMP_STATE

http://oaspub.epa.gov/waters/state_rept.control?p_state=PA

Palustrine and Wetland Communities Inventory

Palustrine and Wetland Communities on State Forest Land.
Palustrine Forest Types Acres
Black Spruce-Tamarack Peatland 85
Bottomland Oak-Hardwood Palustrine 335
Hemlock Palustrine 2,274
Hemlock-Mixed Hardwood Palustrine 6,247
Miscellaneous Palustrine/Floodplain 503
Red Maple-Black Ash Palustrine 4
Red Maple-Black Gum Palustrine 1,219
Red Maple-Elm-Willow Floodplain Swamp 24
Red Spruce Palustrine 1,236
Red Spruce-Mixed Hardwood Palustrine 145
Silver Maple Floodplain 16
Sycamore-(River Birch)-Box Elder Floodplain 583
Sub-total 12,671
Palustrine Woodlands, Shrublands, and Openings  
Palustrine Scrub-Shrub 3,380
Palustrine Woodland 5,156
Emergent Wetland 2,529
Bog-Fen 636
Sub-total 11,702
Total Acres of Palustrine and Wetland Communities 24,373

 

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Spring Seeps and Vernal Ponds Inventory

Spring seeps and vernal ponds will be inventoried per the Landscape Examination process. This inventory will result in a GIS layer of spring seeps and vernal ponds.

Aquatic Community Classification

An aquatic community classification project is currently underway in Pennsylvania by the Natural Heritage program including The Nature Conservancy, the Western Pennsylvania Conservancy and the Department of Conservation and Natural Resources, Bureau of Forestry. The Pennsylvania Aquatic Community Classification Project (project) proposes to develop and apply standardized aquatic ecosystem classifications and reference conditions, which will allow conservation planners to identify, characterize, and map existing locations of freshwater plants and animals and their habitats across the state and to then assess their relative conservation priority. The project will help identify the highest priority areas for aquatic resource protection as well as augment and strengthen statewide conservation programs while providing important data to watershed groups and other organizations to assist local watershed planning, protection and restoration efforts. For more information on the project refer to the Fauna Resources Section of this plan.

 

Policy Statement

Water Resources Management involves all water resources, values, uses, functions, and delineations. The Bureau of Forestry will manage water resources within the context of ecosystem management, considering the wide range of potential impacts, issues, and opportunities relating to water resources.

Goals and Objectives

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Goal 1: Protect and enhance water resources to produce the highest-quality water possible from state forest lands.
  Objective 1: Protect surface and ground water quality.
  Objective 2: Restore the quality of degraded surface and ground water resources where possible.
  Objective 3: Protect and manage surface and groundwater resources for potable water production.
Goal 2: Protect, manage, and enhance riparian ecosystems.
  Objective 1: Minimize impacts to riparian ecosystems when planning and implementing management activities.
  Objective 2: Form partnerships with other agencies and organizations to assist with developing a riparian ecosystem evaluation and monitoring program.
  Objective 3: Restore degraded riparian ecosystems where possible.
Goal 3: Protect, manage, and enhance aquatic ecosystems.
  Objective 1: Minimize impacts to aquatic ecosystems when planning and implementing management activities.
  Objective 2:

Form partnerships with other agencies and organizations to assist with developing an aquatic ecosystem monitoring and evaluation program designed to:

  • Develop a classification system for aquatic ecosystems on state forest lands.
  • Investigate aquatic ecosystem evaluation in inventory and landscape examination procedures.
  • Include an evaluation of aquatic ecosystem issues in the Environmental Review process
  Objective 3: Attempt to restore deficient aquatic ecosystems to a healthy state wherever possible.
  Objective 4: Provide habitat for a diversity of native aquatic life.
  Objective 5: Protect aquatic species of concern (refer to Flora and Fauna Sections for specific actions and guidelines).
  Objective 6: Protect wetlands.
Goal 4: Manage water resources for "in-stream" values and functions such as recreation, aesthetic enjoyment, and habitat for aquatic ecosystems.
  Objectives: Refer to the Objectives listed for Goal # 3 as well as the Goals and Objectives of the Recreation Section of the State Forest Resource Management Plan.

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Guidelines and Actions

The Bureau of Forestry has developed both general and specific management guidelines designed to maintain and/or enhance water resources, values, uses, and functions, and also to protect riparian and aquatic ecosystems from sedimentation, thermal, and chemical pollution. The Bureau of Forestry approached this task by developing a diverse set of guidelines considering management zoning, best management practices (BMPs), and restricting certain activities in specific areas. The following guidelines apply to all management activities occurring on state forest land; variance from these guidelines requires the prior written approval of the State Forester. The guidelines for managing water resources are organized by the following subject areas:

  • Environmental Reviews
  • General Guidelines for Managing Water Resources
  • Zoning Guidelines for Considering Water Resources
  • Guidelines for Managing Municipal Watersheds
  • Guidelines for Special Protection Waters
  • Guidelines for Protecting Spring Seeps and Vernal Ponds
  • Guidelines for Activities in Wetlands, Aquatic Ecosystems, and Riparian Ecosystems
  • Guidelines for Groundwater Conservation and Protection
  • Guidelines for Coordinating Water Resources Management with Other Management Considerations

Environmental Reviews

A written Environmental Review must be completed for the following types of projects having the potential to affect water resources:

  • Wetlands encroachment
  • In-stream alterations for aquatic habitat improvements
  • Groundwater well drilling
  • Bridge construction
  • Herbicide treatments in aquatic ecosystems

General Guidelines for Managing Water Resources

The following general guidelines apply to any management activity on state forest land.

A All activities will require close and constant supervision by the District Forester or delegated representative. The District Forester reserves the right to suspend operations if impacts to water resources are likely. The District Forester is responsible for maintaining periodic contact with local municipalities regarding future water needs and plans.
B.

All soil-disturbing management activities must be implemented according to procedures outlined in the Silviculture Manual and Oil and Gas Guidelines. Soil Erosion and Sedimentation Control Plans will be developed and implement for all applicable activities. All management activities will meet or exceed the recommendations for best management practices outlined in the following three documents, which provide guidelines for implementing BMPs:

  1. Best Management Practices for Pennsylvania Forests, Shelby Chunko, Editor.
  2. Controlling Erosion and Sedimentation from Timber Harvesting Operations, Penn State and DEP (formerly DER), Bureau of Land and Water Conservation
  3. Best Management Practices for Silvicultural Activities in Pennsylvania's Forested Wetlands, Darlene B. Brown, Editor.
C. Compartment soil maps (GIS when available) should be consulted for the presence of highly erodible soils or soils with severe equipment limitations. Special precautions apply for such areas. See Soil Resources section.
D. Disturbed areas such as skid roads, haul roads, log decks, etc., should be confined to 5% or less of the sale area.
E. Roads and trails must be located away from stream courses except where stream crossings cannot be avoided. The distance between stream and roads and/or trails should be 50 feet plus 4 feet for each one percent of slope; thus a 20% slope between road and stream would require (20% x 4') + 50 feet, or 130 feet from the stream. Refer to the Guidelines for Special Protection Waters for additional restrictions.
F. Stream crossings should be avoided whenever possible. When a road or skid trail must cross a watercourse (small springs, spring seeps and intermittent streams), closed culverts or bridges must be used.
G.

Fords are prohibited on all streams in watersheds used by municipalities, institutions, and private users for potable water supply and on Wilderness Trout Streams/Exceptional Value Waters. The use of fords at stream crossings for truck transportation (skidding logs is prohibited) of forest products is a last resort on all other watersheds and will be permitted by the State Forester only if it is not feasible to construct a bridge or install a culvert. The following conditions must apply:

  1. Stream width prohibits bridge construction cost.
  2. Stream has solid bottom and approaches that contain rock, stone or gravel.
  3. Additional tonnage of rock, stone or gravel for a minimum distance of 50 feet to be applied on approaches with intercepting dips or culverts to prevent stream sedimentation.
  4. Ford location is at right angle to the stream channel.
  5. No objection to fording the stream by the Pennsylvania Fish and Boat Commission.
H. The maximum grade on all roads and heavily used skid trails should be less than 10%. The optimum grade is between 4% and 10% to minimize erosion and reduce transportation cost of removing forest products from the sale area.
I. Roads must be drained adequately by cross drains with culverts or broad-based intercepting dips. Refer to the Silviculture Manual.
J. Roads, log landings, skid trails, and oil, gas, and mineral sites should be constructed only during dry weather.
K. Log landings should be constructed at least 200 feet from streams, ponds, lakes and marshes to reduce the risk of sedimentation. Special diversions and sedimentation basins should be installed as necessary.
L. An approved gate should be installed at the entrance of main timber sale haul roads, oil and gas access roads, and other administrative roads prior to operations beginning to protect the road system from erosion caused by unauthorized vehicles.
M. Logging operations should be kept away from the streams to prevent soil disturbance near the stream. Trees cut below the level of the road should be moved uphill with a winch.
N. In critical locations such as excessively wet areas, stream bottoms and highly erodible soils, logging operations should be restricted or confined to the summer months.
O. Portable sawmill, chipper, and de-barker sites must be located no closer to a watercourse than 300 feet plus 10 feet for each percent slope between the site and stream and shall be located no closer than one mile to an intake or impounding reservoir. Exceptions must be approved by the State Forester with concurrence by the Department of Environmental Protection, Bureau of Water Quality Management and the Bureau of Community Environmental Control. Refer to the Guidelines for Municipal Watersheds and Guidelines for Special Protection Waters for additional restrictions.
P. Herbaceous cover (consult with the Ecological Services Section for wildlife planting recommendations) should be established on portions of disturbed areas subject to erosion prior to or as quickly as possible to comply with the Silviculture Manual and Oil and Gas Guidelines
Q. Rights-of-way shall be constructed to minimize damage to the forest, while maintaining the functionality of the right-of-way.
R. Pesticides must be applied according to the label recommendations and per specifications outlined in the Silviculture and Forest Health Manuals. All proposed applications of pesticides having the potential to affect aquatic resources must be submitted to the Fisheries Resource Biologist, Bureau of Fisheries and Engineering, PA Fish and Boat Commission, for review.
S. S. District personnel should monitor stream conditions whenever possible when performing field duties. If a pollution event (or potential event) from sedimentation, thermal, or chemical sources is suspected, personnel should immediately report the location, nature, and extent of the event to the District Forester, Ecological Services Section, DEP, PAFBC, or any other agency with jurisdiction.
T.

For sanitary guidelines:

Per the Bureau of Forestry's Camping Policy for State Forest Land:

  • All camping should be at least 100 feet from any stream or other open water source.
  • All field privies (individual use or slit trench latrines) must be at least 200 feet from a lake, stream, spring, or other open water source. Self-contained portable toilets are required to be used at designated campsites.

Refer to the Leased Campsite Manual for policies on outhouse construction and placement at leased campsites.

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Zoning Guidelines for Considering Water Resources

It is a policy of the Bureau of Forestry to zone all state forest lands according to the primary land use and land use capability, and to apply management practices that will protect and enhance the values for which the land was zoned. Examples of how water resource values are protected through the Bureau of Forestry's seven management zones are discussed below. Refer to the Land Classification and Management Zoning Manual for additional information.

Natural and Wild Area Management Zones

Natural Areas have been designated to protect specific unique scenic, historic, geologic and ecological values. Wild Areas cover extensive areas designed to provide forest users the opportunity to pursue recreation activities in remote and relatively undisturbed settings. By excluding most management activities, Natural and Wild Areas afford the greatest protection of water resources.

Aesthetic/Buffer Management Zone

Connectivity, aesthetics, and water quality conservation are the primary values associated with the Aesthetic/Buffer Management Zone. The following minimum buffer zones are designed to protect water resources by limiting operations within riparian zones:

  1. Exceptional value waters: will have a 100-foot aesthetic/buffer management zone on both sides of the stream. Only salvage cutting will be permitted within this zone.
  2. High quality waters: will have a 100-foot aesthetic/buffer management zone on both sides of the stream.
  3. Perennial cold water streams: will have a 100-foot aesthetic/buffer management zone on both sides of the stream.
  4. Wilderness trout streams: will have a 200-foot aesthetic/buffer management zone on both sides of the stream. Only salvage cutting will be permitted within this zone.
  5. Warm water streams: will have a 100-foot aesthetic/buffer management zone on both sides of the stream.
  6. Wild rivers: The assigned stream corridor will be zoned aesthetic/buffer management zone. Only salvage cutting will be permitted within 200 feet of both sides of the stream.
  7. Scenic rivers: The assigned stream corridor will be zoned aesthetic/buffer management zone. Only salvage cutting will be permitted within 100 feet of both sides of the stream.
  8. Recreational rivers: will have a 100-foot aesthetic/buffer management zone on both sides of the stream.
  9. Modified recreational rivers: will have a 100-foot aesthetic/buffer management zone on both sides of the stream.
  10. Pastoral rivers: will have a 100-foot aesthetic/buffer management zone on both sides of the stream.
  11. Lakes, Ponds and Impoundments: will have a 100-foot aesthetic/buffer management zone around their perimeter.

Limited Resource Management Zone

The Limited Resource Management Zone limits management activities, such as timber harvesting and recreation development, on sites with steep slopes, surface rocks or other features affecting operability.

Multiple Resource Management Zone

The Multiple Resource Management Zone is applied to areas where timber, water, recreation, fauna, flora and minerals are the major values. This comprises the majority of lands within the State Forest system and is the least restrictive, most encompassing management zone. Appropriate BMPs will be followed during all management activities.

During the harvest allocation planning process for the Multiple Resource and Commercial land base, an area reduction factor of 10% was applied to reduce the available area for harvest to account for areas that are too rocky, too wet, or too steep and too small to small have been classified as a separate stand. This reduction factor will help to protect sensitive areas within the multiple resource and commercial land base.

Special Resource Management Zone

The Special Resource Management Zone is applied to areas managed for specific values such as public plant sanctuaries, special wildlife management areas, certain recreation sites, vistas, and reservoirs. Appropriate BMPs will be followed in these zones, which will have specific management recommendations or plans, depending on the values that are being recognized.

Anthropogenic Site Management Zone

Anthropogenic management zone applies to areas where human influence on the natural setting is most apparent, such as roads, rights-of-ways, mineral sites, tower sites, leases, forest district buildings, etc. Appropriate BMPs will be followed in theses zones.

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Guidelines for Managing Municipal Watersheds

Recognizing the importance and need for water, the Conservation and Natural Resources Act states, "The Department of Conservation and Natural Resources shall have the power: to give to boroughs and other municipalities of this Commonwealth, upon such terms and subject to such restrictions and regulations as the Department may deem proper, the privilege of impounding water and drilling water wells upon any state forest, and of constructing, maintaining and operating lines of pipes upon and through state forests for the purpose of conveying water therefrom, wherever it shall be to the public interest so to do".

The management of municipal watersheds is aimed at correcting past problems, such as the immediate removal of pollution sources and soil stabilization in problem areas, and at preventing future problems from arising. This is done by prohibiting possible pollution sources from becoming established, and by controlling the management of the other forest resources to prevent soil erosion and sedimentation.

The management of potential municipal watersheds is aimed at the gradual removal of pollution sources, at prohibiting potential pollution sources from becoming established, and at controlling permanent physical development to avoid future erosion and sedimentation problems.

The following guidelines are designed to provide specific protection to municipal watersheds on state forest land.

Timber Harvesting in Municipal Watersheds

Timber management will be permitted on municipal watersheds, but with restrictions to protect water quality. Research has shown that removing trees through silvicultural practices can increase water yields of forested watersheds. For the present management period, the Bureau of Forestry does not plan to implement management activities specifically designed to increase water yield; however, this could be necessary in the future.

The following guidelines apply, in addition to all other water resources guidelines, when a proposed state forest timber sale is located upstream from a dam or impounding basin on a watershed that supplies water to a municipality, institution or others for domestic, industrial or recreational use:

A.

A. When the stand analyses have been completed, the District Forester shall notify the proper authority by certified, return-receipt mail. The special precautions that will be taken by the Bureau of Forestry to protect the watershed during the logging operations, how the timber sale will affect the watershed, and a deadline for reply (at least 30 days), should be included in the notification. The District Forester shall send Regional Sanitarian a copy of the same information forwarded to a municipality, institution or private user.

  1. If no reply is received from authority by deadline date, the District Forester shall attempt to contact the authority by telephone or in person in order to ascertain reactions to the sale and request a letter confirming the same. If the letter of confirmation is not received from authority, the District Forester shall assume that the authority has no objections and proceed with the sale.
  2. If the reply from authority offers no objections, the District Forester may proceed with the sale.
  3. If reply from authority objects to the sale, the District Forester shall contact the authority to discuss the matter further in order to resolve the objection. If objection is resolved, the authority should confirm this in a letter to District Forester. If objection is not resolved, the District Forester shall forward his recommendation to the Silviculture Section who will notify the District Forester whether or not sale should be processed.
  4. Copies of all letters to and from each authority should be submitted immediately by the District Forester to the Silviculture Section.
B.

The sale proposal forwarded to the Silviculture Section shall include a report containing the following information:

  1. The location and owner or lessee of each recreational area, dam or impounding basin and of the land immediately adjoining each dam or impounding basin provided the abandonment of same has been confirmed by owner's or lessee's letter to the District Forester.
  2. The distance each dam, recreational area or impounding basin is located downstream from the nearest boundary of the proposed sale.
  3. A list of special precautions that should be taken by the Bureau of Forestry to protect the recreational area, watershed or water supply and, if applicable, an explanation how the proposed timber sale will improve the watershed or water supply when, in the opinion of the District Forester, proposed timber sale will affect the watershed or water supply.
  4. A statement describing how the proposed timber sale will affect the recreational area, watershed or water supply.
C.

Upon receipt of the sale proposal from the District Forester, the Silviculture Section shall decide if the proposed sale area and watershed shall be inspected by the District Forester in conjunction with the watershed authority involved before approval is granted.

  1. If the proposed sale is approved, the Silviculture Section will notify the District Forester to proceed with the sale.
  2. If the proposed sale is not approved the Silviculture Section will notify the District Forester accordingly.
D. D. When the proposed timber sale is located on a watershed that does not supply water to a municipality, institution or others for domestic, industrial or recreational use, the word "none" shall be entered under total sale area opposite municipal watershed on Form FMT -5 or under area opposite watershed on Form FMT -4.
E.

E. Timber management on municipality, institutional, and private watersheds must follow the same criteria that are required for logging on all watersheds, along with the following additional restrictions:

  1. An approved metal gate should be installed at the entrance of a main haul road prior to logging operations to protect the road system from erosion caused by unauthorized vehicles.
  2. Portable sawmill sites within a municipality, institutional, or private watershed must be located no closer than one mile to the intake or impounding reservoir.
  3. Herbaceous cover must be established on all large disturbed areas such as portable sawmill sites, roads, log landings, and skid trails subject to erosion either prior to or as quickly as possible after sale termination to comply with the Silviculture Manual.

Oil, Gas, and Mineral Activities in Municipal Watersheds

Oil, gas, and mineral activities in municipal watersheds will be implemented in a manner that eliminates or minimizes impacts to water resources and protects municipal water sources. These activities must be reviewed independently for each resource to be extracted, for each watershed and for each location within the watershed. An Environmental Review must be completed for proposed oil, gas, and mineral activities in municipal watersheds. In addition to the standard 21 items, this review should consider circumstances such as mineral ownership (if minerals are reserved, we may not be able to prevent their extraction); benefits to be gained by the Commonwealth (e.g., land reclamation); or economic value of the resource (e.g., loss of gas because of migration); and the possible adverse effects on the watershed.

Refer to the Oil and Gas Lease as well as the Guidelines for Administering the Oil and Gas Lease for specific operating guidelines.

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Recreation Development and Activities in Municipal Watersheds

Recreation management and activities will be implemented in a manner that eliminates or minimizes potential pollution and sedimentation threats. The following guidelines apply specifically to recreation-related management and activities in municipal watersheds:

A. Existing campsite leases must be inspected at each lease renewal by the local Sewage Enforcement Officer to ensure that the sanitary system complies with present Department of Environmental Protection regulations.
B. Under present Department of Environmental Protection regulations, recreational uses (such as swimming, fishing, camping and motor-boating) having the potential of discharging pollutants into a municipal water supply are permitted only where the water supply receives full treatment; (i.e., chemical addition, coagulation, filtration and disinfection).
C. New trailside shelters or structures will be prohibited.
D. Construction of recreation access roads through existing or potential municipal watersheds should be kept to a minimum.
E. Vehicular trails through both existing and potential watersheds must comply with the same standards of construction as in the Silviculture Manual with the exception that water bars will not be permitted and a more narrow right-of-way and running surface may be used.
F. No shallow water impoundments for wildlife will be constructed within existing and potential municipal watersheds where the water does not receive full treatment.

Guidelines for Special Protection Waters

Under Title 25, Pennsylvania Code, Chapter 93. Water Quality Standards, all waters within the Commonwealth have been classified according to present condition and use. Waters receiving special protection include High Quality Waters (HQ) and Exceptional Value Waters (EV). HQ and EV waters are defined as follows:

HQ: "A stream or watershed which has excellent quality waters and environmental or other features that require special water quality protection."
EV: "A stream or watershed which constitutes an outstanding national, State, regional or local resource, such as waters of national, State or county parks or forests, or waters which are used as a source of unfiltered potable water supply, or waters of wildlife refuges or State game lands, or waters which have been characterized by the Fish Commission as 'Wilderness Trout Streams,' and other waters of substantial recreational or ecological significance."

HQ waters are subject to the same anti-degradation water quality restrictions as EV waters. The difference is that no water quality degradation is permitted of EV waters, but degradation is permitted of HQ waters for justifiable social and economic reasons. Water quality criteria have been established for each classification delineating the limits of metals, dissolved oxygen, pH. temperature, turbidity, etc. that can occur within the streams in each class. EV waters are an exception because specific criteria for levels of pollutants were not established but rather an "existing quality or "antidegradation" criteria was established which specifies that no pollutants can be discharged into a stream of that class. This means that no human-made or human-caused activity can change the temperature, increase the turbidity or change the pH of the stream.

The Pennsylvania Fish and Boat Commission established The Wilderness Trout Streams Program "to protect and promote native trout fisheries, the ecological requirements necessary for natural reproduction of trout and wilderness aesthetics." Streams classified as Wilderness Trout Streams also meet the standards for EV waters.

In addition to all other guidelines for protecting water resources, the following guidelines have been developed for Wilderness Trout Streams, HQ, and EV waters:

A. HQ Waters: 100-foot aesthetic/buffer management zone on both sides of the stream.
B. EV Waters: 100-foot aesthetic/buffer management zone on both sides of the stream. Salvage cutting only is permitted within this zone.
C. Wilderness Trout Streams: 200-foot aesthetic/buffer management zone on both sides of the stream. Salvage cutting (or cutting for human safety) only is permitted within this zone.
D.

Access: A roadless zone where public motor vehicle traffic is excluded should be established for one-fourth mile on each side of the stream. The length of the roadless zone should be no less than two miles. Topographic or other physical features may dictate consideration of a narrower roadless zone. Existing woods roads can be closed gated to vehicular traffic in order to create a roadless zone. After considering all alternatives, existing roads may be closed providing campsite lessees or private interior landowners do not use the road.

All existing roads within the roadless zone may be used for administrative purposes and shall be gated to exclude public motor vehicles. New access roads needed for resource management can be constructed within the roadless zone providing the roads are gated and posted to exclude public motor vehicles.

E. Roads and trails for any purpose will be located away from the stream course. The distance between the stream and a parallel road or trail shall be 200 feet plus four feet for each one percent of slope.
F. For HQ waters, culverts and bridges are permitted if they can be installed with minimal disturbance to the streambed and banks. For EV waters and Wilderness Trout Streams, culverts are permitted only on small tributary streams (averaging less than ten feet in width prior to June 15 of any year) and no closer than 200 yards of the main stream. For EV waters and Wilderness Trout Streams bridges are permitted only if they can be installed without equipment entering the stream channel during construction, or if stream crossings with equipment are limited to one occasion.
G. No fill can be placed in the stream channel and no bank alterations will be permitted.
H. Fords are not permitted on HQ and EV waters or Wilderness Trout Streams.
I. Roads and trails within one-quarter mile of all intermittent and perennial streams will be restored upon termination according to procedures outlined in the Silviculture Manual and Oil and Gas Guidelines, recommendations provided by the Ecological Services Section, or in such a manner as designated or approved by the District Forester.
J. An approved metal gate must be installed at the entrance of main haul roads and oil and gas access roads to protect road systems from erosion by unauthorized vehicles.
K.

Portable sawmill sites and debarking or chipping operations are not permitted within:

  • 300 feet plus 10 feet for each percent slope of HQ waters
  • One-quarter mile of EV waters and Wilderness Trout Streams
L. Construction of pipeline and power line corridors in riparian areas should be avoided whenever possible. When they cannot be avoided, all disturbed areas adjacent to the stream will be restored per procedures outlined in the Silviculture Manual and Oil and Gas Guidelines and recommendations provided by the Ecological Services Section. Mulch will be applied to seeded areas on slopes greater than 15 percent.
M. Pipeline stream crossings will be permitted only after proper review by the DEP Bureau of Watershed Management. An Environmental Review must be completed for all rights-of-way.
N. Power line crossings of streams will be permitted. Rights-of-way should be as narrow as possible within the riparian buffer. A screen of small trees or tall shrubs should either be maintained or planted within the 200-foot zone. If the trees on an electric transmission right-of-way will not interfere with the power line, the 200-foot buffer should not be disturbed.
O. Well-drilling sites must be located 300 feet from HQ and EV waters and Wilderness Trout Streams and 200 feet from all other streams or water bodies. Refer to the Oil and Gas Guidelines for specific details.
P. Strip-mining will not be permitted within one-quarter mile of each side of the stream in areas where the Commonwealth owns the mineral rights.
Q. Exceptions to the foregoing management requirements can be granted by joint approval of the State Forester and the Director of the DEP Bureau of Water Quality Management. Exceptions will be granted only for justifiable social or economic reasons.

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Guidelines for Protecting Spring Seeps and Vernal Ponds

Spring seeps and vernal ponds are highly diverse and valuable components of our forest ecosystems in Pennsylvania. Spring seeps are important to wildlife as they provide a variety of food sources during periods of snow cover in addition to the diversity of species associated with the forested wetland habitat they create. Vernal ponds support a diversity of species not found elsewhere in the forest including many invertebrates such as fairy shrimp. These ponds also are critical to the life cycles of many amphibians, which make up the largest vertebrate biomass in the forest and perform many vital functions. Proper management of these aquatic ecosystems is critical.

The ecosystems dependent upon spring seeps and vernal ponds are sensitive to disruption. Some important management considerations should be remembered to protect the integrity of these systems. Shading is important on both spring seeps and vernal ponds, especially in the maintenance of the unique vegetation associated with forested wetlands. High temperatures resulting from increased insolation are a problem for the amphibians using vernal ponds. Sedimentation is detrimental to both of these systems. Ruts in the vicinity of spring seeps can disrupt water flow. Ruts around vernal ponds can disrupt the migratory patterns of amphibians, or cause the amphibians to breed in undesirable bodies of water, which may dry up too soon.

Spring seeps and vernal ponds are considered "jurisdictional wetlands," and as such, fall under the regulatory process. The following guidelines clarify management questions regarding these sensitive areas, and should serve well to protect these valuable resources. Zoning variances will be granted, where justified, upon approval by the State Forester. If you have any questions or comments regarding these recommendations, please contact the Ecological Services Section or the Resource Planning and Information Division.

A. Spring Seep Management
  A spring seep is a permanent spring where water emerges from the ground and flows across the soil surface without defined bed and banks. The limits of the seep are demarked by the extent of surface water.
  Guidelines:
  1. 100 foot buffer zone to retain shading, prevent erosion, and ensure water flow:
    a. Maintain a 10-foot wide "no disturbance" buffer around the perimeter of the seep.
    b. Manage an additional 90-foot buffer around the "no disturbance" area in where at least 50% canopy closure or a minimum basal area of 60 square feet of live trees is retained.
      1). Retain cavity trees within buffer.
      2). Avoid disturbing soil and leaf litter within the buffer; harvest under frozen or dry conditions when possible; any ruts created within the buffer must be graded or raked to the original contour.
  2. Fell trees away from seeps; leave tops in wetland if they fall into standing water.
  3. Where property boundaries and topography permit, locate roads and heavy-use recreational trails at least 150 feet down slope from head of seep; avoid roads within 150 feet uphill of seep. If topography does not permit recreational trails to be routed around the seep, elevate or stabilize trail surface as appropriate to ensure water flow and soil stability.
  4. Encourage herbaceous vegetation around and below seeps and retain all valuable food producing small tree and shrub species in the vicinity of seeps, especially those seeps that remain open through the winter. Establish wildlife food shrubs and coniferous cover near seeps if needed.
B. Vernal Pond Management
  A vernal pond is a small, temporary body of water in a depression fed by surface runoff and maintained by a high water table (does not persist year-round). Also called ephemeral, fluctuating pools.
  Guidelines:
  1. 200-foot buffer zone to retain shading and minimize soil and leaf litter disturbance.
    a. Maintain a 100-foot wide "no disturbance" buffer around the perimeter of the pond.
    b. Manage an additional 100-foot buffer around the "no disturbance" area in which is retained at least 50% canopy closure or a minimum basal area of 60 square feet of live tree.
      1). Restrict cutting operations within buffer to November through January.
      2). Any ruts created within the buffer must be graded or raked to the original contour.
      3). Recreational trails may be located within the buffer, provided the trail does not cause an influx of sediment into the pond.

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Guidelines for Activities in Wetlands, Aquatic Ecosystems, and Riparian Ecosystems

A. Wetlands:
  1. All wetlands will be protected or enhanced.
  2. Proposed activities in wetlands will undergo an Environmental Review, as detailed in the Overview Section of the State Forest Resource Management Plan, prior to implementation.
  3. Wetlands will be inventoried and evaluated according to the Landscape Examination procedures.
  4. Wetlands may be created or developed in suitable areas. An Environmental Review must be completed. Consult the Ecological Services Section. Other sources of information include the PA Game Commission, PA Fish and Boat Commission, PA DEP Bureau of Watershed Management, USDA Natural Resource Conservation Service.
B. In-stream Restoration and Improvement
  1. All in-stream alterations require an Environmental Review and an encroachment permit from DEP Bureau of Watershed Management and the notification and, in certain instances, the approval of the PA Fish and Boat Commission.
  2.

In-stream debris or litter should be removed whenever such debris might:

  • Increase the rate of silt deposition or cause an alteration to the existing channel.
  • Prevent fish passage, particularly from larger bodies of warm water into smaller, colder, feeder streams.
  • Slow the rate of flow and thereby contribute to the warming of a trout stream above 58ºF. Small, shallow, low-gradient streams are particularly susceptible to warming because their flow is easily obstructed and they have relatively sensitive thermal regimes.
  3. In-stream activities that might result in silt washing downstream should be prohibited, unless an erosion and sedimentation control plan has been filed and approved.
C. Riparian Zone Maintenance, Restoration, and Improvement
  1. Stabilize eroding stream banks to prevent siltation and to provide shelter. Seed exposed banks and plant tolerant woody species such as willow, alders or silky dogwood. Consult with the Ecological Services Section for riparian zone seeding and planting recommendations.
  2. When natural disturbances (fire, windthrow, flood, or defoliation) result in the removal of the riparian zone canopy, attempts should be made to restore the riparian zone as soon as possible. Refer to number 1 above.
  3. Uneven-aged management (where applicable) in riparian zones will help to decrease the probability of windthrow by removing high-risk trees. If windthrow occurs, consider severing the root system from the tree and allowing the stump and roots to fall back into their former position. Trees cut within 50-feet of the stream should be winched out.
  4. Roads and rights-of-way should be located away from stream courses. The filter strip between a stream and road or right-of-way should be 50 feet plus 4 feet for each one percent of slope.
  5. Stream crossing should be avoided whenever possible. All roads that must cross watercourses, even small springs and seeps, must be constructed utilizing closed culverts, bridges or at approved fords. Stream crossings should be at a right angle to the stream. Refer to the Silviculture Manual for stream-crossing specifications.
  6. Drilling sites or mineral excavation should not be located within 200 feet of a stream or impoundment. Refer to the Oil and Gas Guidelines for additional information regarding oil and gas development.

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Guidelines for Groundwater Conservation and Protection

Groundwater Sources of Information

The Internet provides access to a wealth of information on groundwater resources in Pennsylvania:

1.

The PA DCNR, Bureau of Topographic and Geologic Survey provides background information on the geology of Pennsylvania's groundwater, water well information, along with links to other data, information, agencies, and organizations devoted to groundwater protection and management.

http://www.dcnr.state.pa.us/topogeo/groundwater/groundwater.htm

 

2.

The PA DEP, Bureau of Watershed Management provides guidelines for protecting groundwater resources as well as information regarding water well regulations and permits.

http://www.dep.state.pa.us/dep/deputate/watermgt/wc/subjects/srceprot/default.htm#gw_protect
http://www.dep.state.pa.us/dep/deputate/watermgt/watermgt.htm

 

3. The United States Geologic Survey (USGS) provides online real-time and historic groundwater information on streams and water wells across Pennsylvania.

http://pa.water.usgs.gov/

Groundwater Wellhead Protection Guidelines (Based on DEP's Wellhead Protection Program)

A legal mandate of the state forest system is to provide potable water, and thus, the Bureau of Forestry is committed to protecting drinking water sources. Due to strict water-quality standards and the expense associated with treating water from surface sources, increasingly, local municipalities are relying on groundwater. In certain rural areas, state forest land is the first choice for municipalities to drill high-yield water wells. Therefore, the Bureau of Forestry will take every measure possible to ensure the protection of groundwater resources, particularly those serving as public water sources. Protecting groundwater resources is critical, because if contamination occurs, it is very costly and difficult to employ remedial activities, and if polluted, groundwater often remains contaminated for a long period of time.

The DEP's Wellhead Protection Program (WHPP) is a proactive effort designed to protect groundwater supplies. The underlying principle of the program is that it is much less expensive to protect groundwater than it is to try to restore it once it becomes contaminated. The Bureau of Forestry will cooperate with DEP and local municipalities in efforts to implement water wellhead protection guidelines to protect groundwater supplies and recharge areas.

Wellhead Protection Area (WHPA)

A WHPA is defined as the surface and subsurface area surrounding a public water supply well, wellfield, spring or infiltration gallery through which contaminants are reasonably likely to move toward and reach the water source. Chapter 109 currently establishes three zones of protection for wellhead protection areas:

  1. Zone I is the immediate area surrounding the source, which may range from a radius of 100 to 400 feet depending on site-specific source and aquifer characteristics.
  2. Zone II is a radius of one-half mile, unless a more detailed delineation is established to identify the surface area overlying the portion of the aquifer through which water is diverted to a well or flows to a spring or infiltration gallery (capture zone for a well; note that this is not the same as the zone of influence).
  3. Zone III is an area that contributes surface water or groundwater to Zone II that may be significant to protecting the well. Collectively, Zone II and Zone III constitute the contributing area of the well.

The figure below illustrates the concept of wellhead protection zones.

Graphic depicting the concept of wellhead protection zones
Source: DEP, Bureau of Watershed Management

The Bureau of Forestry will cooperate with other local municipalities (water supplier) and agency experts (DEP, DCNR Topo-Geo, USGS) in efforts to implement the following guidelines for managing water wellhead protection zones:

Zone I: 100-400 Foot Radius

  1. Prohibit management activities or land uses having the potential to adversely impact the water quality or quantity. Examples include, but are not limited to wastewater disposal, stormwater basins, parking lots, permanent structures, heavily traveled roads, etc.
  2. Prohibit the storage, use, or disposal of potential contaminants, unless the chemical or material is used in the production or treatment of drinking water.
  3. Prohibit the storage of liquid fossil fuels (except if used as an auxiliary power source for a public water supply system).
  4. Timber sale and oil and gas access roads with heavy truck traffic, and public-use roads with heavy traffic should not be located in Zone I. Minor, less used skid trails and public-use roads could be permitted, depending on the particular site.
  5. Cooperate with local municipalities and agency experts in efforts to develop specific protection guidelines for Zone I for specific wells.
  6. Identify existing and potential sources of contamination.
  7. Comply with all other guidelines for protecting water resources.

Zone II: One-half Mile Radius

  1. Cooperate with local municipalities and agency experts in efforts to delineate (map) the one-half mile radius protection zone.
  2. Cooperate with local municipalities and agency experts in efforts to develop specific protection guidelines for Zone II for specific wells.
  3. Identify existing and potential sources of contamination.
  4. Comply with all other guidelines for protecting water resources.

Zone III: Area Contributing Surface or Groundwater.

  1. Cooperate with local municipalities and agency experts in efforts to delineate (map) Zone III.
  2. Cooperate with local municipalities and agency experts in efforts to develop specific protection guidelines for Zone III for specific wells.
  3. Identify existing and potential sources of contamination.
  4. Comply with all other guidelines for protecting water resources.

Impacts to the Larger Forest Ecosystem

Except for wellhead protection zones, most of the water resources guidelines are aimed at protecting surface water. However, because most streamflow is derived from groundwater, management activities in groundwater recharge areas have implications for both surface and groundwater. Activities such as mining, oil and gas well drilling, and other surface activities that generate pollutants have the most potential to cause groundwater degradation. Plans for these activities should be evaluated carefully, and then closely monitored. Refer to the Oil and Gas Guidelines and Oil and Gas Lease for information on protecting groundwater during oil and gas drilling operations.

Groundwater resources will be managed as part of the larger hydrologic system. In addition to managing wellhead protection zones to protect the groundwater resource, the Bureau of Forestry is also concerned with potential negative impacts to the larger forest ecosystem resulting from over-developing groundwater resources. When considering requests for drilling groundwater wells, the Bureau of Forestry will work with agency experts to assess the well's potential impact to the surrounding forest ecosystem. Watersheds have varying tolerances to varying levels of groundwater development. The Bureau of Forestry will cooperate with agency experts to ensure that additional wells in certain watersheds will not adversely impact the water resources within that particular watershed. The Bureau of Forestry will work closely with local municipalities and agency experts to conduct thorough site assessments for individual water wells as well regional planning efforts considering local water needs and the available water supply.

Guidelines for Coordinating Water Resources Management with Other Management Considerations

A. The District Forester is responsible for coordinating water resources management activities with other resources, uses, and values of state forest land.
B. Management activities must be in accordance with the area's land-use zoning. Requests for variation from the designated land use must be fully justified in writing to the State Forester.
C. If Federal- or State-listed fauna or flora species of concern, or habitat critical to their survival, either presently known or subsequently identified, occur within or adjacent to a proposed watershed project area, the Ecological Services Section must be notified prior to commencement of additional work on the project. The Ecological Services Section will determine what, if any, changes to the project are necessary to protect the species or habitat.
D. If archaeological sites, either presently known or subsequently identified, occur within a proposed watershed project area, the Silviculture Section will be notified prior to commencement of additional work on the project. The Silviculture Section will coordinate assessment of the site and needed protection measures with the State Historical and Museum Commission.

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Actions for Goals and Objectives

Goal 1: Protect and enhance water resources to produce the highest-quality water possible from state forest lands.
  Objective 1: Protect surface and ground water quality.
 

Actions:

  1. Modify guidelines and practices as needed to protect water quality.
  2. Develop and implement site-specific erosion and sedimentation control plans.
  3. Develop and implement best management practices.
  4. Consider potential impacts to water quality when planning management activities.
  5. Implement storm water runoff control for all bureau facilities and activities.
  6. Monitor activities on state forest lands to insure that water quality is being adequately safeguarded.
  Objective 2:
Restore the quality of degraded surface and ground water resources where possible.
 

Actions:

  1. Identify and inventory resources with degraded water quality.
  2. Prioritize mitigation and track areas needing remedial work in a systematic and uniform manner.
  3. Form partnerships with other agencies and organizations for technical and financial assistance for water quality restoration projects.
  4. Support research for water quality restoration.
  Objective 3: Protect and manage surface and groundwater resources for potable water production.
 

Actions:

  1. Coordinate with other agencies and organizations on watershed management and planning activities.
  2. Follow the Guidelines for Managing Water Resources.
  3. Modify guidelines and practices as needed to protect potable water sources.
  4. Maintain an inventory of existing potable water sources.
  5. Cooperate with agencies such as the USGS and DCNR, Bureau of Topographic and Geologic Survey to develop hydrologic budgets and groundwater inventories for state forest land. Initial inventories could include 1) current groundwater use; 2) how much groundwater is available; and 3) water-bearing characteristics of the rocks underlying state forest land?
  6. Cooperate with agencies such as the USGS and DCNR, Bureau of Topographic and Geologic Survey to identify and inventory potential potable water sources, including groundwater recharge areas, on state forest lands.
  7. Identify and form partnerships with communities and municipalities potentially needing state forest land for potable water
  8. Manage the development of groundwater resources (refer to groundwater guidelines), while considering potential impacts to surface and groundwater systems and the larger forest ecosystem.
  9. Consider potential impacts to potable water resources when planning management activities.
Goal 2: Protect, manage, and enhance riparian ecosystems.
  Objective 1: Minimize impacts to riparian ecosystems when planning and implementing management activities.
 

Actions:

  1. Follow the Guidelines for Managing Water Resources.
  2. Modify guidelines and practices as needed to protect riparian ecosystems.
  Objective 2: Form partnerships with other agencies and organizations to assist with developing a riparian ecosystem evaluation and monitoring program.
 

Actions:

  1. Form partnerships with other agencies and organizations to assist with developing an evaluation and monitoring program of riparian ecosystems on state forest lands.
  2. Include riparian ecosystem evaluation in inventory and landscape examination procedures.
  3. Include an evaluation of riparian ecosystem issues when planning management activities.
  Objective 3: Restore degraded riparian ecosystems where possible.
 

Actions:

  1. Form partnerships with other agencies and organizations to assist with developing a program to:
  • Identify and evaluate streams with degraded or missing forest riparian buffers on state forest lands.
  • Prioritize and plan mitigation work
  • Monitor and track riparian buffers needing remedial work, in a systematic and uniform manner.
Goal 3: Protect, manage, and enhance aquatic ecosystems.
  Objective 1: Minimize impacts to aquatic ecosystems when planning and implementing management activities.
 

Actions:

  1. Refer to the Guidelines for Activities in Wetlands, Aquatic Habitats Ecosystems, and Riparian Habitats Ecosystems.
  2. Follow the Guidelines for Managing Water Resources.
  3. Modify guidelines and practices as needed to protect riparian ecosystems.
  Objective 2:

Form partnerships with other agencies and organizations to assist with developing an aquatic ecosystem monitoring and evaluation program designed to:

  • Develop a classification system for aquatic ecosystems on state forest lands.
  • Include aquatic ecosystem evaluation in inventory and landscape examination procedures.
  • Include an evaluation of aquatic ecosystem issues in the planning of all management activities.
  • Monitor and evaluate activities that could reasonably impact aquatic ecosystems, and modify practices to protect the aquatic ecosystems.
  Objective 3: Attempt to restore deficient aquatic ecosystems to a healthy state where possible.
 

Actions:

  1. Form partnerships with other agencies and organizations to assist with developing a program to:
  • Locate and evaluate degraded water bodies on state forest lands.
  • Prioritize and plan mitigation work and track water bodies needing remedial work, in a systematic and uniform manner.
  Objective 4: Provide habitat for a diversity of native aquatic life.
 

Actions:

  1. Complete baseline inventories of aquatic life within lake, pond, and stream ecosystems.
  2. Consider potential impacts to aquatic habitats when planning management activities.
  Objective 5: Protect aquatic species of concern (Refer to Flora and Fauna Sections for specific actions and guidelines).
  Objective 6: Protect wetlands.
 

Actions:

  1. Inventory and evaluate wetlands per Landscape Exam procedures.
  2. Conduct Environmental Reviews for activities involving wetlands encroachment.
Goal 4: Manage water resources for "in-stream" values and functions such as recreation, aesthetic enjoyment, and habitat for aquatic ecosystems.
 

Actions:

  1. Refer to Goal 3 above regarding Aquatic Ecosystems as well as the Fauna Section of the State Forest Resource Management Plan for information on aquatic habitat management.
  2. Refer to the Recreation Section of the State Forest Resource Management Plan for specific objectives, actions, and guidelines pertaining to recreation management.
  3. Follow the Guidelines for Managing Water Resources.
  4. Determine primary uses for water bodies in high recreation use areas.

 

Monitoring

Indicators:

  • Extent of area by forest community type in protected area categories.
  • Area treated with herbicide, pesticides, fertilizer, etc. (herbicide / fertilizer treatment lists / maps, insect suppression lists / maps)
  • Number of sites where illegally deposited waste is a problem
  • Percent of water bodies in forest areas (e.g. stream miles, lake acreage) with significant impairment.
  • Mechanisms in-place to provide opportunities for public input in decision-making related to state forest management.
  • Central depository for data collection, monitoring efforts and research are in place.
  • Level of expenditure on research, information and education monitored.
  • User Days (from district specific inventories & surveys).

 

Critical Research Needs

  • Inventories of ground water resources.
  • Impacts of groundwater development on forest ecosystems, including surface water systems
  • Baseline data for monitoring changes to biological diversity, pH, dissolved oxygen, chemical levels, sedimentation, temperature change
  • Baseline chemical analysis data for lakes and ponds (streams?)
  • Aquatic life inventories
  • Effects of trout stocking on native flora and fauna

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