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WATER RESOURCES
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.
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.
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.
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.
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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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:
- Produce the greatest possible sustained supply of timber products.
- 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.
- 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.
- Develop and preserve the recreational values of the forests.
- Protect the watersheds from erosion and obtain
from them the maximum yields of useable water.
- 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:
- Restricting or limiting activities and development on watersheds
to practices that will neither reduce the quantity nor impair the quality
of the water.
- Analyzing future water needs of communities within or near state
forest lands and designating potential watersheds that can be developed
to fill those needs.
- 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.
- 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.
- 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.
- 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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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
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.
| 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

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.

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.
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)
|
Back to Top
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 |
Back to Top
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.
http://www.dep.state.pa.us/dep/deputate/watermgt/WC/Subjects/WSNoteBks/shedtable.htm

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 |
Back to Top
Groundwater Sources of Information
The Internet provides access to a wealth of information on groundwater
resources in Pennsylvania:
- 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 |

| 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/
|
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 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 will be inventoried per the Landscape Examination
process. This inventory will result in a GIS layer of spring seeps and
vernal ponds.
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.
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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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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
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
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:
- Best Management Practices for Pennsylvania Forests, Shelby Chunko,
Editor.
- Controlling Erosion and Sedimentation from Timber Harvesting
Operations, Penn State and DEP (formerly DER), Bureau of Land
and Water Conservation
- 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:
- Stream width prohibits bridge construction cost.
- Stream has solid bottom and approaches that contain rock, stone
or gravel.
- 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.
- Ford location is at right angle to the stream channel.
- 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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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:
- 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.
- High quality waters: will have a 100-foot aesthetic/buffer
management zone on both sides of the stream.
- Perennial cold water streams: will have a 100-foot aesthetic/buffer
management zone on both sides of the stream.
- 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.
- Warm water streams: will have a 100-foot aesthetic/buffer
management zone on both sides of the stream.
- 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.
- 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.
- Recreational rivers: will have a 100-foot aesthetic/buffer
management zone on both sides of the stream.
- Modified recreational rivers: will have a 100-foot aesthetic/buffer
management zone on both sides of the stream.
- Pastoral rivers: will have a 100-foot aesthetic/buffer management
zone on both sides of the stream.
- 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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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 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.
- 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.
- If the reply from authority offers no objections, the District
Forester may proceed with the sale.
- 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.
- 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:
- 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.
- The distance each dam, recreational area or impounding basin
is located downstream from the nearest boundary of the proposed
sale.
- 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.
- 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.
- If the proposed sale is approved, the Silviculture Section
will notify the District Forester to proceed with the sale.
- 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:
- 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.
- Portable sawmill sites within a municipality, institutional,
or private watershed must be located no closer than one mile to
the intake or impounding reservoir.
- 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 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.
Back to Top
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.
|
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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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.
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Guidelines:
|
| |
1. |
100 foot buffer zone to retain shading, prevent erosion,
and ensure water flow:
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| |
|
a. |
Maintain a 10-foot wide "no disturbance"
buffer around the perimeter of the seep.
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| |
|
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.
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| |
|
|
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.
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| |
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.
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| |
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
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| |
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.
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| |
|
|
2). |
Any ruts created within the buffer must be graded or
raked to the original contour.
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| |
|
|
3). |
Recreational trails may be located within the buffer,
provided the trail does not cause an influx of sediment into the pond. |
Back to Top
| A. |
Wetlands:
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| |
1. |
All wetlands will be protected or enhanced.
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| |
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.
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| |
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.
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| B. |
In-stream Restoration and Improvement
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| |
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.
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| |
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.
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| |
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. |
Back to Top
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:
- 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.
- 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).
- 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.

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
- 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.
- Prohibit the storage, use, or disposal of potential contaminants,
unless the chemical or material is used in the production or treatment
of drinking water.
- Prohibit the storage of liquid fossil fuels (except if used as an
auxiliary power source for a public water supply system).
- 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.
- Cooperate with local municipalities and agency experts in efforts
to develop specific protection guidelines for Zone I for specific wells.
- Identify existing and potential sources of contamination.
- Comply with all other guidelines for protecting water resources.
Zone II: One-half Mile Radius
- Cooperate with local municipalities and agency experts in efforts
to delineate (map) the one-half mile radius protection zone.
- Cooperate with local municipalities and agency experts in efforts
to develop specific protection guidelines for Zone II for specific wells.
- Identify existing and potential sources of contamination.
- Comply with all other guidelines for protecting water resources.
Zone III: Area Contributing Surface or Groundwater.
- Cooperate with local municipalities and agency experts in efforts
to delineate (map) Zone III.
- Cooperate with local municipalities and agency experts in efforts
to develop specific protection guidelines for Zone III for specific
wells.
- Identify existing and potential sources of contamination.
- 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.
| 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. |
Back to Top
| 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:
- Modify guidelines and practices as needed to protect water
quality.
- Develop and implement site-specific erosion and sedimentation
control plans.
- Develop and implement best management practices.
- Consider potential impacts to water quality when planning management
activities.
- Implement storm water runoff control for all bureau facilities
and activities.
- 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:
- Identify and inventory resources with degraded water quality.
- Prioritize mitigation and track areas needing remedial work
in a systematic and uniform manner.
- Form partnerships with other agencies and organizations for
technical and financial assistance for water quality restoration
projects.
- Support research for water quality restoration.
|
| |
Objective 3: |
Protect and manage surface and groundwater resources
for potable water production.
|
| |
Actions:
- Coordinate with other agencies and organizations on watershed
management and planning activities.
- Follow the Guidelines for Managing Water Resources.
- Modify guidelines and practices as needed to protect potable
water sources.
- Maintain an inventory of existing potable water sources.
- 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?
- 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.
- Identify and form partnerships with communities and municipalities
potentially needing state forest land for potable water
- Manage the development of groundwater resources (refer to groundwater
guidelines), while considering potential impacts to surface and
groundwater systems and the larger forest ecosystem.
- 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:
- Follow the Guidelines for Managing Water Resources.
- 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:
- Form partnerships with other agencies and organizations to
assist with developing an evaluation and monitoring program of
riparian ecosystems on state forest lands.
- Include riparian ecosystem evaluation in inventory and landscape
examination procedures.
- Include an evaluation of riparian ecosystem issues when planning
management activities.
|
| |
Objective 3: |
Restore degraded riparian ecosystems where possible.
|
| |
Actions:
- 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:
- Refer to the Guidelines for Activities in Wetlands, Aquatic
Habitats Ecosystems, and Riparian Habitats Ecosystems.
- Follow the Guidelines for Managing Water Resources.
- 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:
- 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:
- Complete baseline inventories of aquatic life within lake,
pond, and stream ecosystems.
- 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:
- Inventory and evaluate wetlands per Landscape Exam procedures.
- 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:
- 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.
- Refer to the Recreation Section of the State Forest Resource
Management Plan for specific objectives, actions, and guidelines
pertaining to recreation management.
- Follow the Guidelines for Managing Water Resources.
- Determine primary uses for water bodies in high recreation use
areas.
|
- 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).
- 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
Back to Top
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