Ontario Ministry of Natural Resources
Information and Resource Management, Sudbury District
November 2004

Ce document est seulement disponsible en anglais.

Approval statement

I am pleased to approve this Statement of Conservation Interest (SCI) for Eden Township Forest Conservation Reserve (C157).

Eden Township Forest Conservation Reserve represents the best example in the area of red pine and cedar dominated forest on a landscape of low hills. The site also contains a provincially significant representation of sparse coniferous forest on prehistoric lake sediments. Regulated on November 22, 2002, this 145 hectare conservation reserve is situated in Eden Township, approximately 15 kilometres southwest of the downtown core of the City of Greater Sudbury.

Direction for establishing, planning and managing conservation reserves is defined under the Public Lands Act, the Crown Land Use Policy Atlas, the Ontario’s Living Legacy Land Use Strategy and other applicable policies. The specific direction for managing this conservation reserve is in the form of a basic SCI, which defines the area to which the plan applies, provides the purpose for which the conservation reserve has been proposed, and outlines the Ministry of Natural Resources' management intent for the protected area. This SCI has been created with input from program specialists within the Sudbury District. It will provide both the foundation for the continued monitoring of activities and guidance for the management of the conservation reserve. More detailed direction at this time is not anticipated. However, should significant facility development be considered or complex issues arise requiring additional studies, more detailed management direction in the form of special protection measures, or a detailed Resource Management Plan, will be prepared with full public consultation.

Public and Aboriginal consultation occurred prior to the regulation of this conservation reserve. An additional 30-day consultation period took place in October, 2004 that provided stakeholders with an opportunity to comment on the draft SCI. Comments from the review period have been considered in the development of this document.

The management guidelines outlined in this SCI will be implemented by the Sudbury Area Supervisor, and will be reviewed every five years and amended as required by the District Planner, Sudbury District, and Ministry of Natural Resources.

Prepared by:
Joey Young, Mike Jackson
Crown Land and Protected Areas Planning Assistants
Date: November 2004

Recommended For Approval by:
Ernie Heerschap for
Stephen Devos
A/Sudbury Area Supervisor
Date: 18/01/2005

Cindy Blancher-Smith
District Manager, Sudbury District
Date: 31/01/2005

Approved by:
Rob Galloway
Regional Director, Northeast Region
Date: 09/02/2005

Executive summary

The purpose of this Statement of Conservation Interest is to identify and describe the natural, recreational, and cultural values of Eden Township Forest Conservation Reserve and to outline and guide the Ministry of Natural Resources' management intent for this area.

Eden Township Forest Conservation Reserve (C157) was regulated on November 22, 2002. The 145 hectare conservation reserve is situated in Eden Township and is located approximately 15 kilometres southwest of the downtown core of the City of Greater Sudbury. The administrative details of the site are summarized in Table 1 below.

Eden Township Forest Conservation Reserve represents the best example in the area of red pine and cedar dominated forest on a landscape of low hills. The site also contains a provincially significant representation of sparse coniferous forest on prehistoric lake sediments. The protection of these features is considered paramount and, as such, any future management decisions that affect these values will require a thorough evaluation to ensure that the value remains protected.

The Ontario Ministry of Natural Resources, Sudbury District, and Sudbury Area will be responsible for implementing the management policies and guidelines for Eden Forest Conservation Reserve. Their primary role will be to provide public information and compliance monitoring to ensure adherence to current policies and guidelines.

Table 1: Administrative details for Eden Township Forest Conservation Reserve (C157).

OMNR Administrative Region/District/AreaNortheast Region/Sudbury District/Sudbury Area
Site Region–Site District (Hills 1959)5E-4 Sudbury
Ecoregion–Ecodistrict (Crins and Uhlig 2000)5E-4
TownshipEden
Topographical Map Number / Name41 I/06 Copper Cliff
UTM Co-ordinatesZone 17 (NAD 83) 489500 E, 5130500 N
Latitude/Longitude46˚19'42"N / 81˚08'06"W
OBM Numbers2017480051300, 2017490051300, 2017480051200, 2017490051200
Nearest TownApproximately 15 km southwest of the City of Greater Sudbury
Altitude230-340 m
Area145 ha
Wildlife Management Unit42
Forest Management UnitSudbury Forest
Watershed2 CF of the Lake Huron basin
RegulatedNovember 22, 2002
Ontario GazetteDecember 7, 2002
SCI CompletedJanuary 30, 2005

1.0 Introduction

The following document is a Statement of Conservation Interest (SCI) for Eden Township Forest Conservation Reserve (C157). The purpose of this SCI is to identify and describe the natural, recreational, and cultural values of Eden Township Forest Conservation Reserve and to outline the Ministry of Natural Resources' management intent for this area. The first three sections of this document highlight the provincial context in which it was produced, state its goal and objectives, and summarize the planning process for conservation reserves. Sections 4.0 through 7.0 are specific to Eden Township Forest Conservation Reserve and provide background information and management direction for the site. Section 8.0 outlines the requirements for continued implementation and review of this document.

Management direction specified in this SCI will serve to protect the conservation reserve for the benefit of all Ontario residents. This direction will comply with the land use intent and guidelines stated in the Crown Land Use Policy Atlas (CLUPA) on the internet at /page/crown-land-use-policy-atlas. The CLUPA is a consolidation of existing local land use policies for Crown lands within the Ontario Living Legacy Land Use Strategy (LUS) (1999) planning area, an area that covers 45 percent of the province and that extends from Lake Simcoe in the south to the Albany River in the north. Additionally, this conservation reserve will be managed under the Public Lands Act (R.S.O. 1990, C.P.43), and will comply with all legal requirements as specified under the Environmental Assessment Act (R.S.O. 1990, c.E.18).

Eden Township Forest Conservation Reserve was selected to protect the best example in the area of red pine (Pinus resinosa) and white cedar (Thuja occidentalis) dominated forests on a landscape of low hills. The protection of this feature is considered paramount and, as such, any future management decisions that affect this value will require a thorough evaluation to ensure that the value remains protected.

The Ontario Ministry of Natural Resources, Sudbury District, and Sudbury Area will be responsible for implementing the management policies and guidelines for Eden Township Forest Conservation Reserve. Their primary role will be to provide public information and compliance monitoring to ensure adherence to current policies and guidelines.

2.0 Goal and objectives of the SCI

2.1 Goal

The goal of this SCI is to provide the framework and the direction to guide management decisions affecting Eden Township Forest Conservation Reserve while protecting natural heritage values and permitting land use.

2.2 Objectives

The following objectives are identified as the means to achieve the above stated goal:

2.2.1 Short term objectives

  • To describe the site’s current state of the resource in terms of its values and existing uses and activities.
  • To outline the Ministry of Natural Resources' management intent for the protected area.
  • To determine the land use compatibility of current land uses, and to develop specific guidelines and prescriptions to manage these uses.
  • To provide direction for the evaluation of proposed new uses or economic ventures through the application of the Test of Compatibility (Appendix D) and applicable Environmental Assessment Act (e.g., the Class Environmental Assessment (EA) for Provincial Parks and Conservation Reserves) legislation.

2.2.2 Long term objectives

  • To maintain the conservation reserve in as natural state as possible.
  • To identify research and/or monitoring strategies that may contribute to sound long-term management of the conservation reserve.
  • To create public awareness of the values within this conservation reserve by providing information on the resources it contains and protects, and to support responsible stewardship through partnerships with local stakeholders.

3.0 Management planning

3.1 Provincial context

Ontario’s network of protected areas has been established to conserve representative areas of the province’s natural diversity (which includes species, habitats, landforms, and ecological systems). Protected natural heritage areas are a key component in the sustainable management of natural resources, ensuring that representative sites within the larger managed landscape are retained in as natural a state as possible.

On July 16, 1999, the Ontario’s Living Legacy Land Use Strategy (LUS) (OMNR 1999) was released to guide the planning and management of much of Ontario’s Crown lands. Extensive consultation was conducted during the development of the LUS. The objectives of the LUS were to complete Ontario’s system of parks and protected areas; recognize the land use needs of the resource-based tourism industry; provide forestry, mining and other resource industries with greater certainty around land and resource use; and, enhance hunting, angling and other Crown land recreational opportunities.

These areas are considered to have significant features and values or are representative of major landforms and vegetation types. As such, they require protection from incompatible activities in order for their values to endure over time. Eden Township Forest Conservation Reserve was created during this expansion and now forms part of Ontario’s network of natural heritage areas. The site was selected to represent the best example in the area of red pine and cedar dominated forests on a landscape of low hills. The site has also been found to contain a provincially significant representation (1 ha) of sparse coniferous forest on prehistoric lake sediments, which contributes to the target (50 ha) to be protected within the ecodistrict.

The Ontario Ministry of Natural Resources has established conservation reserves as a tool to protect natural heritage values on Crown lands, while permitting most traditional Crown land uses to continue. These uses include recreational activities, such as hunting and fishing. Lands designated as conservation reserves in the LUS (OMNR 1999) are removed from the Sustainable Forest License area and mining and surface rights are withdrawn from staking under the Mining Act (RSO 1990 Chapter M.14).

The Crown Land Use Policy Atlas (CLUPA), available on the internet at /page/crown-land-use-policy-atlas, is a consolidation of existing Crown land use policies and is now the official source for guidance on the management of Crown land and protected areas (OMNR 2004).

3.2 Planning for a conservation reserve

The planning process for a conservation reserve consists of regulating the site and preparing a site-specific management plan. Consultation with the public, aboriginal communities and industry occur during site identification, boundary finalization, and management planning. Regulation of a conservation reserve involves the preparation of a legal description of site boundaries, the removal of the site from the Sustainable Forest Licence area, and the withdrawal of the site from staking under the Mining Act (RSO 1990 Chapter M.14). Once a conservation reserve is regulated, the level of management planning required to fulfill the protection targets is determined, and a basic Statement of Conservation Interest (SCI), enhanced SCI or a Resource Management Plan (RMP) is prepared.

A basic SCI is prepared when there is no deviation from the land use direction provided in the LUS (OMNR 1999) and there are few to no issues that require resolution. Alternatively, a RMP is prepared in situations where one or more complex issues have to be addressed, and/or where there is widespread public interest in a site. An enhanced SCI is an intermediary document which is used when a site requires more detailed management direction than would be provided by a basic SCI, but does not have issues significant enough to warrant the preparation of a RMP. Whichever the determination, the plan must be completed within three years of the conservation reserve’s regulation date. The guidelines for the preparation of these documents are provided in Procedural Guidelines A – Resource Management Planning (OMNR 1997) and the Northeastern Region Guidelines on the Planning Process for Conservation Reserves: Statement of Conservation Interest and Resource Management Plan (Thompson 2001).

A SCI is a management plan guided by the policy direction contained in the CLUPA (see Appendix C). The purpose of a SCI is to identify the state of the resource in terms of the site’s values and its current land use activities, and to outline the Ministry of Natural Resources' management intent for the conservation reserve. Basic SCI's typically have a 30-day public consultation period, whereas enhanced SCI's and RMP's have a longer consultation period. Upon completion of this public review, the SCI or RMP is revised as necessary and approved by the Regional Director, MNR Northeast Region.

Existing permitted uses within conservation reserves may continue, unless they are shown to have a significant negative impact on the values protected by the site. A review/evaluation mechanism is in place to address new permitted uses or land use proposals. The Test of Compatibility (Appendix D), as outlined in the Conservation Reserves Policy PL3.03.05 (OMNR 1997a) and Environmental Assessment Act legislation will be used to screen proposals. Once approved, the Class Environmental Assessment for Provincial Parks and Conservation Reserves (OMNR 2003) will be used to screen most project proposals and management activities occurring within the conservation reserve.

Where cultural resources may be impacted, proposals may be screened through Conserving a Future for our Past: Archaeology, Land Use Planning & Development in Ontario, Section 3 (MCzCR 1997).

Public comment may be solicited during a review of any future land use proposals that require new decisions to be made. Appropriate Environmental Assessment Act (R.S.O. 1990, c.E.18) requirements and amendment processes (e.g. Environmental Bill of Rights posting, CLUPA amendment) will apply to any future proposal and/or any significant change in management direction being considered for a site.

3.3 Planning process for Eden Township Forest Conservation Reserve

3.3.1 Boundary refinement and regulation

The Eden Township Forest Conservation Reserve was proposed as a conservation reserve in the LUS (OMNR 1999). A letter, fact sheet and proposed boundary map were mailed to stakeholders and to interested members of the public during the boundary consultation process. Consultation occurred with the general public, aboriginal communities, and industry, and the boundary of the site was regulated through an amendment to Ontario Regulation 805/94 of the Public Lands Act on November 22, 2002, by Ontario Regulation 313/02. The official Ontario Gazette amendment is available on the internet at http://www.ontariogazette.gov.on.ca/ in volume 135, issue 49 on December 7, 2002.

3.3.2 Planning area

The planning area for this SCI consists of the regulated boundary for Eden Township Forest Conservation Reserve (see Figure 1). However, to fully protect values within the conservation reserve, the area beyond the regulated boundary may require additional consideration through landowner outreach programs when adjacent land uses pose potential negative impacts on the conservation reserve. Crown land areas beyond the regulated boundary may also require additional consideration when larger land use planning initiatives, such as forest management planning, pose potential negative impacts on the site.

3.3.3 Consultation and significant land use issues

To date, no significant issues related to land use in this area have been identified. For this reason, it was determined that a basic SCI will adequately identify the site’s significant features and serve as the appropriate format for providing management direction. It should be noted that this document addresses only those issues or land use proposals currently known to the Ministry of Natural Resources, Sudbury District. The direction provided by this SCI, and future management decisions, will work to resolve any potential land use conflicts and ensure that identified values continue to be adequately protected.

This SCI has been created with input from program specialists at the area, district, regional and provincial levels of the Ministry of Natural Resources. Public, aboriginal communities and industry were also provided an opportunity to comment on a draft of this SCI. A public consultation period took place October 13th, 2004 to November 13th, 2004. Notification of this review period occurred via an information package mailed to affected stakeholders and an advertisement that appeared in local newspapers. Comments received during this period were considered in the refinement of this document. Upon approval of this SCI, public notification will occur via mail-out to interested stakeholders and a notice will appear in the same newspapers.

4.0 Background information

4.1 Location and site description

Eden Township Forest Conservation Reserve is located approximately 15 km southwest of the old City of Sudbury. The site can be found on the southern shore, near the southwest end of Long Lake, near the southern municipal boundary of the City of Greater Sudbury. This site is situated entirely within Eden Township and is 145 hectares in size. Figure 1 illustrates the general location of Eden Township Forest Conservation Reserve.

Figure 1: Site location for Eden Township Forest Conservation Reserve

Site location for Eden Township Forest Conservation Reserve

Enlarge Figure 1: Site location for Eden Township Forest Conservation Reserve

Whenever possible, recognizable natural and cultural features, such as creeks, shorelines or old roads have been used to delineate conservation reserve boundaries to facilitate on-the-ground identification (see Figure 1). The extent of the western boundary of the conservation reserve follows the water’s edge of Long Lake, excluding the parcels of private land and respective shoreline. The south and east boundaries follow cultural features in the form of three patented mining claims.

Eden Township Forest Conservation Reserve is an easily accessible site. The conservation reserve can be found by traveling southwest from Sudbury via Long Lake Road (Regional Road 80) to Tilton Lake Road. From Tilton Lake Road, turn north onto Lakes End Road, a secondary access road, and follow the road for approximately 1 km (see Figure 1). A recreation trail, Broder Dill Snowmobile Association trail #4 (Ontario Federation of Snowmobile Clubs [OFSC] trail C108D), passes through the conservation reserve from the middle of the south boundary to the wetland along the east boundary of the site. Water access to the perimeter of the conservation reserve is also available via Long Lake.

Figure 2: Aerial view of Eden Township Forest: northeast boundary towards the southwest, showing the road going through the site and private cottages along Long Lake.
(Photo taken by B. Burkhardt during aerial flight, OMNR; August 28, 2003)

Photo of Aerial view of Eden Township Forest: northeast boundary towards the southwest, showing the road going through the site and private cottages along Long Lake.

Eden Township Forest Conservation Reserve is located within Ecodistrict1 5E-4 (Hills 1959), an ecological unit which incorporates most of the area comprising the City of Greater Sudbury. Within the conservation reserve is the best example in the area of red pine and eastern cedar dominated forests on a landscape of low hills. White birch (Betula papyrifera), black spruce (Picea mariana) and balsam fir (Abies balsamea) are also common tree species within the site. Figure 2 illustrates the general setting within and surrounding the conservation reserve. A portion of a small wetland is located along the eastern boundary of the site and continues outside of the conservation reserve. Life science and earth science values within the site are further described in subsection 5.2- Natural Heritage Values.

4.2 Site history

Much of the area surrounding Sudbury (including the area of Eden Township Forest Conservation Reserve) has been influenced by logging and mining operations which began in the mid nineteenth century. Subsequently, a number of settlers became situated in the Long Lake area during the early 1900's, to pursue farming and lumber activities (Cudmore et al. 2004). The Victoria Harbour Logging Company had a mill on the eastern part of Long Lake. In 1912, the Long Lake Gold Mine, which operated from 1909-1916 at the southern extent of Long Lake, was the largest gold producing mine in Ontario (City of Greater Sudbury 2004).

During the mid-1900's, smelting emissions from nickel production changed the chemical composition of soil and water, causing vegetation to die and exposing massive tracts of land around the Sudbury area to erosion (Cudmore et al. 2004).

The City of Greater Sudbury (2004) indicates that several artefacts (i.e. chert, flint-like projectile tip; quartzite knife) were found on the shores of Long Lake, which suggests that ancient people lived and hunted in the Sudbury area.

4.3 Socio-economic interest

Eden Township Forest Conservation Reserve is in close proximity to the municipality of the City of Greater Sudbury. The employment base of the region surrounding the City of Greater Sudbury is dependent on the natural resources of the area. Mining, forestry, trapping and resource-based tourism have been essential to the historical growth and development of the area.

Active Bear Management Area, trapline and baitfish harvesting operations occur in the area; as well, hunting are activities in the general area that are part of the local economy.

The site is potentially important to local residents for outdoor recreational opportunities, because of its close proximity to a large urban centre. The designation of this area as a conservation reserve allows for managed free-use of the area, while protecting the natural heritage values of the site for future generations.

The conservation reserve lies within the Robinson-Huron Treaty Area #9 and is in close proximity to the Whitefish Lake First Nation. Protection of this area ensures that activities traditionally carried out by First Nation communities in this Treaty Area will be able to continue.

4.4 Inventories

Table 2 indicates the current status of natural heritage inventories that have occurred for Eden Township Forest Conservation Reserve. Recommendations for future inventory needs are located in Table 3, section 7.02- Recommendations.

Table 2: Inventory and survey information for Eden Township Forest Conservation Reserve.

Type of InventoryInventory MethodDate(s) of InventoryReport
Life ScienceAerial reconnaissance28 Aug. 2004Cudmore, W., Copeland, C. and Longyear S. 2004. Eden Township Forest Conservation Reserve (C157) Natural Heritage Area - Life Science Checksheet. Unpublished Information. Ontario Ministry of Natural Resources.
Earth ScienceAerial photo interpretation28 Aug. 2004Kristjansson, R.J. 2004. Earth Science Inventory Checklist for C157 Eden Township Forest Conservation Reserve. Unpublished Information. Ontario Ministry of Natural Resources.
RecreationGround and aerial reconnaissanceGround: 9 July 2004 29 July 2004 Air: 28 Aug. 2003Jackson, M. Eden Township Forest Conservation Reserve (C157) Recreation Resource Inventory Report. Unpublished Information. Ontario Ministry of Natural Resources.

5.0 State of the resource

Descriptions in this section are not necessarily complete. If new values key or otherwise are identified, they will be added to this document as an amendment. If any new value is considered significant, management guidelines may be modified, if required, to ensure its protection.

5.1 Key values

Key values are values that make this site unique and have led to its designation as a conservation reserve. Their protection is paramount. The key values of the Eden Township Forest Conservation Reserve include the following:

  • The best example in the area of red pine and cedar dominated forests on a landscape of low hills.
  • A provincially significant representation of sparse coniferous forest on prehistoric lake sediments.

Additional values, listed in subsection 5.2- Natural Heritage Values, are also important features and activities identified within the site.

5.2 Natural heritage values

5.2.1 Earth science values

5.2.1a Regional landforms

Eden Township Forest Conservation Reserve is found within Ecodistrict 5E-4 of Ecoregion 5E (Georgian Bay) (Hills 1959; Crins & Uhlig 2000). The ecodistrict is characterized by moderate to small-sized pockets of water-laid silt and sand, sand and gravel plains, as well as bedrock outcrops shallowly covered by stony sand and stone-free silt. The coarse sand is granitic and the lime content of the fine-silty sand varies from granitic to a trace of lime. The bedrock has weakly, moderately, and in one instance strongly broken relief. Landforms within the ecoregion consist of lowland areas of water-laid materials frequently broken by bedrock outcrops, and upland areas of rolling bedrocks covered to variable depths with materials ranging from gravel to silty sands. The soil type includes brown podsolic and weakly developed podsols on sandy soils of the upland areas and limy clays and silts of the lowland areas (Hills 1959; Cudmore and Longyear 2004).

5.2.1b Surficial geology

Rik Kristjansson (2004), MNR provincial geospecialist, verified that the conservation reserve’s surficial geology is dominated by bedrock controlled uplands. The bedrock-drift complexes are areas of moderate bedrock exposure with a discontinuous cover of till. Ice-contact stratified drift deposits (unit 4) have been deposited against the bedrock upland in the southwest part of the site. Glaciolacustrine deposits (unit 6) occur in the southeast and southwest lowland areas and organic deposits (unit 9) are associated with the wetlands in the southeast. The geological features are common in the ecoregion and are of local significance only.

Eroded soils are common in the area of the City of Greater Sudbury, due to extensive disturbance such as cutting, fire and smelter fumes. Shorelines along Long Lake consist of a mix of rock outcrops, silty sands and cobble rock (Cudmore and Longyear 2004).

5.2.1c Bedrock geology

Bedrock is the dominant landform in the conservation reserve (Map 2, Appendix A). The morphology of the bedrock surface is dominated by bedrock knob (or knoll) forms with intervening, lower elevation areas. Moderate bedrock exposure associated with a discontinuous cover of till is anticipated within this area of bedrock-drift complex (Kristjansson 2004).

5.2.2 Life science values

5.2.2a Regional ecology

Eden Township Forest Conservation Reserve is found within Ecodistrict 5E-4 of Ecoregion 5E (Georgian Bay) (Hills 1959; Crins & Uhlig 2000). Vegetation in this region typically consists of sugar maple (Acer saccharum), yellow birch (Betula alleghaniensis), eastern hemlock (Tsuga canadensis), and white pine (Pinus strobus) on fresh sites; white spruce (Picea glauca) and balsam fir on fresh clays and cooler valleys mixed with hardwoods at higher altitudes; and black spruce and tamarack (Larix laricina) in cold wet areas. Forest climate for this area is mid- humid, warm-boreal. The area is also located in section L.4e (Sudbury-North Bay) of Rowe’s (1972) Great Lakes – St. Lawrence Forest Region. Extensive disturbance (i.e., forest cutting, forest fires and nickel smelting fumes) has occurred in section L.4e, resulting in the destruction and/or reduction of many naturally occurring species. Presently, pioneer species such as trembling aspen (Populus tremuloides) and white birch occur, with only scattered occurrences of regional characteristic species such as jack pine (Pinus banksiana), sugar maple, yellow birch, red pine, white pine, balsam fir and black spruce.

5.2.2b Vegetation and forest communities

The main forest community within the conservation reserve is red pine-white birch mixedwood stands (Photo 4, Appendix B; Cudmore and Longyear 2004). Maple (Acer species) can also be found in the red pine-white birch mixedwood stand. Mixedwood stands of cedar are also common within the site (see Map 3, Appendix A).

The red pine-white birch community is associated with the ridge located in the northwest portion of the site. This forest community is estimated to be 83 years of age and is essentially the same height. The cedar mixedwood stands are located in the lowlands, south of the ridge and are estimated to be 95 years (Cudmore and Longyear 2004). Under definitions developed by Uhlig et al. (2000), there is no candidate old growth stand within the conservation reserve. There are two distinct sections of age distributions within the site, the cedar mixedwood is 90-119 years of age and the remaining sections are between 60-89 years of age.

The forest communities are not heavily stocked2. The red pine-white birch mixed community is 1-40%, cedar mixedwood is 41-60% and the remaining communities are 61-80% stocked (Cudmore and Longyear 2004).

5.2.2c Fish and wildlife

There are no waterbodies found within the conservation reserve. However, since Long Lake forms a large portion of the boundary of the site, the important sportfish found within Long Lake may be influenced by the conservation reserve, these include: lake trout (Salvelinus namaycush), walleye (Stizostedion vitreum v.), small-mouth bass (Micropterus dolomieu), northern pike (Esox lucius), yellow perch (Perca flavescens) and common sucker (Catostomus spp). Long Lake was stocked with lake trout and small-mouth bass in the mid to late 1970s.

Moose wintering areas have been identified in the area outside of the conservation reserve and management efforts have continued to increase the deer, moose and elk populations (OMNR 2004).

5.2.2d Wetlands and watersheds

A small portion of a wetland (Map 4, Appendix A) is within the site; however, since patented mining claims form the eastern boundary, the majority of the wetland is unable to be protected by the conservation reserve. A basic inventory of the site identified three variations within the wetlands: aligning the creek is a meadow marsh with sedges and cattails; the middle section (aligning the meadow marsh) changes to a thicket swamp with grasses, willow (Salix species), alder (Alnus species) and maple; and, the border of the wetland is a hardwood swamp. The meadow marsh is identified as open muskeg (.5% of the total area) (Photo 6, Appendix B; Cudmore and Longyear 2004).

The conservation reserve is located in the tertiary watershed 2CF of the Lake Huron major basin (OMNR 2002). Long Lake runs along the entire western boundary of the conservation reserve and is classified as a cold water lake.

5.2.2e Species at Risk

No Species at Risk have been identified or documented within the conservation reserve.

5.2.3 Recreational values

Although the conservation reserve is easily accessible, the small size of the site and lack of unique recreational opportunities limits its recreational use. However, a recreation trail (Photo 3, Appendix B), designated in the winter as Broder Dill Snowmobile Association Trail #4 (Ontario Federation of Snowmobile Clubs [OFSC] trail C108D), passes through the conservation reserve from the middle of the southern boundary to the wetland along the eastern boundary of the site. Furthermore, there is a trail that accesses the snowmobile trail from Lakes End Road. ATV use of the access trail has been documented (Figure 3) but no evidence of ATVs travelling to the wetland portion of the snowmobile trail was found.

Figure 3: Entrance to access trail off Lakes End Road.
(Photo taken by Joey Young, OMNR, Aug. 5/04)

Photo shows Entrance to access trail off Lakes End Road.

Eden Township Forest Conservation Reserve is bordered by the Wanapitiei River West General Use Area (G1894). This general use area, which includes portions of Long Lake and Wavy Lake is known for it recreational use. Long Lake is a popular destination for many residents and tourists of the Sudbury area. A number of cottages and residences are adjacent to the conservation reserve and therefore associated recreational uses are thought to occur (e.g. nature appreciation, landscape viewing, swimming, etc…). A beautiful ridge formation along Long Lake is located across from the conservation reserve. Policies for the management of the general land use area are focused on preserving the existing mix of recreational uses, while also managing the local fisheries and wildlife (OMNR 1983, OMNR 2004). To view policies for this conservation area, you may visit the CLUPA at /page/crown-land-use-policy-atlas.

5.2.4 Cultural values

Little is known about the cultural or traditional values of the area contained within this conservation reserve. The conservation reserve is located within the Robinson/Huron Treaty Area #9.

The area contained within the conservation reserve has been traditionally used for resource activities. Intensive forest harvest activities are known to have occurred throughout the area. See section 4.2 – Site History for a more detailed discussion on historical occurrences concerning the conservation reserve.

5.2.5 Research values

No known research activities have occurred within the boundary of Eden Township Forest Conservation Reserve.

5.3 Quality of the resource

5.3.1 Site condition

Site condition refers to the amount of disturbance that the site has experienced to date, including both human and non-human or natural disturbances. The level of disturbance3 in the conservation reserve is considered to be relatively low, as less than 10% of the area is exposed to disturbance (Cudmore and Longyear 2004). The site is exposed to some human disturbance from the cottages that are adjacent to the conservation reserve along Long Lake. There is also a tertiary road running through the conservation reserve that provides access to each private property, via driveways through the site. A utility corridor follows Lakes End Road through the site and provides service to the private camps along Long Lake. A semi-rehabilitated gravel pit is also present in the southwest portion of the conservation reserve.

The conservation reserve serves to protect the best example in the area of red pine and cedar forest on a landscape of low hills (OMNR 2004). The condition of the red pine and cedar forests are in a good state as the disturbance is low in the area; therefore, the site should be ecologically self-contained (Cudmore and Longyear 2004).

Since the early nineteenth century, however the entire ecological region has been impacted by human operations (i.e., logging, prospecting and smelting emissions). The smelting emissions in particular have drastically altered environmental conditions, causing soil and water to become too acidic for many species of vegetation (Cudmore and Longyear 2004).

5.3.2 Diversity

Diversity is a measure of the site’s life and earth science heterogeneity. It is based on the number and range (variety) of the natural landscape features and landforms of earth science values and the richness and evenness of the life science components. The diversity4 rating is based on the landform-vegetation (L:V) combination criteria using geological landform interpretation (Kristjansson 2004), vegetation communities data and taking into consideration the size of the site (Cudmore and Longyear 2004).

Defined in habitat units (HUs), the landform-vegetation combinations include 5 (HUs)on 3 different landforms with the wetland complex on organic deposits adding another landform- vegetation combination, resulting in only 6 landform-vegetation combinations in the conservation reserve (Map 3, Appendix A; Cudmore and Longyear 2004). Therefore, the conservation reserve is considered to have a low diversity rating; although, a thorough geology layer is required to verify the number of landform-vegetation combinations within the site and determine an accurate diversity rating (Cudmore and Longyear 2004).

Evenness5 refers to the proportion of each cover type and its measured area within the conservation reserve. The evenness in the park is very strongly skewed towards three forest communities including: red pine-white birch community (49.7% of total area) and cedar community (23.7% of total area), as well as a mixed hardwood community which covers 11.1% of the total area of the site. The total of the three communities is 83.7%. Development stages add no diversity to the site as the forest communities are fairly even-aged. The age distribution of the forest cover is fairly uniform across the site (30-59 years and 60-89 years) and no candidate old growth stands have been identified (Cudmore and Longyear 2004).

5.3.3 Ecological considerations

Wherever possible, a site’s boundaries should be created to include the greatest diversity of life and earth science features to provide the maximum ecological integrity. It should be ecologically self-contained, bounded by natural features and include adequate area to protect the core ecosystems from adjacent land use activities (OMNR 1992). The conservation reserve has both biological and vectored boundaries. The western boundary has biological boundaries that follow Long Lake mixed with vectored boundaries along the private parcels of land; whereas, the south and eastern boundaries are vectored to exclude areas of patented mining claims. The limits of the conservation reserve are therefore not ecologically self-contained. The site is small, triangular in shape and vectored which weakly protects adjacent land use activities. The core area protected by the conservation reserve is very small and the site fallsfar short of the 2000 ha minimum size standard that Ontario Parks has established for protecting representative natural areas (Cudmore and Longyear 2004).

Recreational activities, in relation to the private properties, could have an impact on the key values of the site due to the cottages' close proximity to the red pine and cedar forests. Also, ATV use of the snowmobile designated recreation trail that leads into the meadow marsh on the eastern boundary of the site may have negative impacts on the wetland. Low impact recreational uses (i.e. hiking and mountain biking) however are not expected to greatly impact the key values of the conservation reserve.

No forest reserves are associated with this site.

6.0 Management guidelines

All management guidelines in this SCI are based on the policy direction contained in the Crown Land Use Policy Atlas (CLUPA). For the most up-to-date version of this policy report, please refer to the CLUPA on the internet at /page/crown-land-use-policy-atlas, or contact your local Ministry of Natural Resources office. A summary table of the management guidelines, outlining permitted uses within the site, is located in Appendix C.

The management guidelines outlined in this section are specific to the Eden Township Forest Conservation Reserve and are intended to protect the site’s unique values. The guidelines in this document are subject to change and may be amended as necessary. If a conflict between management guidelines exists, the conservation reserve will be managed to protect the integrity of its natural values, while permitting compatible land use activities (OMNR 1997).

Proposed new uses and/or development, including research and education activities, will be reviewed on a case-by-case basis. All new proposals will be subject to evaluation under at least one of the following processes: the Test of Compatibility (Appendix D); the Environmental Assessment Act (R.S.O. 1990, c.E.18); and Conserving a Future for our Past: Archaeology, Land Use Planning & Development in Ontario, Section 3 (MCzCR 1997). Once approved, the Class Environmental Assessment for Provincial Parks and Conservation Reserves (OMNR 2003) will be used to screen most proposals and management activities occurring within the conservation reserve.

6.1 First nations

Traditional activities and Aboriginal rights, as defined in the Robinson-Huron Treaty #9 and other applicable legislation, will not be affected by the boundaries of this conservation reserve.

Any First Nation land claims within this area will be addressed according to appropriate Ministry of Natural Resources' procedures. When possible, the Ministry of Natural Resources will work with the Ontario Ministry of Culture to identify archaeological and/or cultural sites to be protected.

6.2 Industrial activities

6.2.1 Commercial timber harvest

The area contained within this conservation reserve (145 ha) has been withdrawn from the Sudbury Forest Sustainable Forest License area and no commercial timber harvesting will be permitted. Please refer to subsection 6.5.3- Non-Commercial Consumptive Resource Use for information regarding non-commercial wood harvesting.

6.2.2 Mining and exploration

There are no existing mining claims or leases within the conservation reserve. Mining and surface rights within the conservation reserve’s boundaries have been withdrawn from staking under the Mining Act (RSO 1990 c.M.14). Mineral exploration is not permitted.

6.2.3 Extraction of peat, soil, aggregate and other material

No extraction operations currently occur within the conservation reserve. New activities for the extraction of peat, soil, aggregate and other material are not permitted.

6.2.4 Energy generation

No energy generation facilities exist within the conservation reserve. New hydropower development and windpower generation operations are not permitted.

6.3 Existing and proposed development

6.3.1 Transportation corridors

6.3.1a Roads

Under the Public Lands Act, section 48 (OMNR 2003a), a road is defined as "a travel corridor that is reasonably capable of allowing travel by motor vehicles licensed to operate on a King’s Highway as defined in the Highway Traffic Act (e.g., personal or commercial cars and trucks)."

Minor maintenance (as defined under Policy PL 3.03.04 [OMNR 2003b]) of existing roads will be permitted provided that maintenance activities do not negatively impact the values being protected by the conservation reserve. Road maintenance activities may be subject to a Test of Compatibility (Appendix D) thru the Environmental Assessment Act.

Lakes End Road is a primary road that is used to access seasonal private properties adjacent to the conservation reserve along Long Lake. Some private access roads have been identified within the conservation reserve and are associated with the private properties adjacent to the site. New private access roads proposed after March 29, 1999 and, for which MNR did not make a commitment, will not be permitted within the conservation reserve.

According to the LUS (OMNR 1999), new roads for resource extraction will not be permitted except for those identified in Forest Management Plans prior to March 31, 1999. No new or existing roads for resource extraction were identified within the conservation reserve prior to this date.

6.3.1b Trails

Under Ontario Regulation 453/96 (OMNR 2003a), a trail is defined as "a path over public lands not used for mineral exploration or extraction." A trail is minor in nature compared to a road, allowing passage of pedestrians, ATVs, snowmobiles or the like (OMNR 2003b).

A recreational trail passes through the conservation reserve from the middle of the southern boundary to the wetland along the eastern boundary of the site. This trail is designated in the winter as a snowmobile trail, Broder Dill Snowmobile Association Trail #4 (Ontario Federation of Snowmobile Clubs [OFSC] trail C108D). ATV use of an access trail to the recreational trail has been documented, though evidence of ATVs travelling to the wetland portion of the snowmobile trail was not found during a recreation inventory of the site (Young pers. comm).

Minor maintenance (as defined under Policy PL 3.03.04 [OMNR 2003b]) of existing trails will be permitted provided that maintenance activities do not negatively impact the values being protected by the conservation reserve. Trail maintenance may be subject to a Test of Compatibility (Appendix D) thru the Environmental Assessment Act.

Any proposed new trails or development of existing trails are subject to the Test of Compatibility (Appendix D) and applicable Ministry of Natural Resources' policies and procedures. Trail development should take into account the unique characteristics of this site and must be compatible with the site’s key values. All existing and new trail heads and trail routes must be recorded using new technologies (i.e. global positioning systems) to ensure an accurate record of the location of the feature. This location information must be provided to the Ministry of Natural Resources, Sudbury District.

6.3.2 Other corridor development/maintenance

A communication and energy transmission line is located within this conservation reserve. The transmission line follows Lakes End Road and is associated with the private residences adjacent to the conservation reserve.

Minor maintenance of the transmission corridor will be permitted provided that maintenance activities do not negatively impact the values being protected by the conservation reserve. Corridor maintenance may also be subject to a Test of Compatibility (Appendix D) should the impact of such activity on the environment be questioned.

New corridor developments will be actively discouraged. Proposals for new corridors will be subject to screening under the Environmental Assessment Act (e.g., the Class Environmental Assessment (EA) for Provincial Parks and Conservation Reserves).

6.3.3 Natural heritage appreciation facilities/recreational structures

There are currently no existing authorized natural heritage appreciation facilities or recreational structures (i.e. boardwalks, bird viewing platforms, kiosks, ski shelters, or interpretative signs) located within the conservation reserve. New public natural heritage appreciation facilities and recreation structures are permitted, subject to the Test of Compatibility (Appendix D) and to screening under the Environmental Assessment Act (e.g., the Class Environmental Assessment (EA) for Provincial Parks and Conservation Reserves).

Facility development should take into account the unique characteristics of this site and must be compatible with the site’s key values

6.3.4 Land disposition

Sale of land is not permitted, except for some types of minor dispositions (e.g. the sale of small parcels of land to provide adequate area for the installation of a septic system), where it does not detrimentally affect the key values of the site. Such sales will be screened under the Test of Compatibility (Appendix D).

Existing leases or LUP's may be renewed or transferred, subject to MNR approval. Private recreation camps may be eligible for enhanced tenure but may not be sold. Permit holders for outpost camps or tourism facilities (e.g., main base lodges) can apply to upgrade tenure from a LUP to a lease.

No Land Use Permits (LUP's) are currently issued within this conservation reserve. New leases or LUP's may be issued for approved public uses (i.e. not for private recreation camps), subject to the Test of Compatibility (Appendix D) and applicable Ministry of Natural Resources' policies and procedures.

6.4 Commercial activities

6.4.1 Commercial bait harvesting

Eden Township is currently allocated for one commercial bait harvesting operation. New operations may be considered subject to the Test of Compatibility (Appendix D) and to screening under the Environmental Assessment Act (e.g., the Class Environmental Assessment (EA) for Provincial Parks and Conservation Reserves).

Any proposed new trails for baitfish harvesting purposes are subject to the Test of Compatibility (Appendix D) and to screening under the Environmental Assessment Act (e.g., the Class Environmental Assessment (EA) for Provincial Parks and Conservation Reserves). Please refer to subsection 6.3.1b – Trails for further information on the establishment and maintenance of new trails and subsection 6.5.5 – ATV and Snowmobile Use for further information on their usage.

6.4.2 Commercial fishing

There are currently no commercial fisheries operating within the conservation reserve. New operations may be considered subject to the Test of Compatibility (Appendix D) and to screening under the Environmental Assessment Act (e.g., the Class Environmental Assessment (EA) for Provincial Parks and Conservation Reserves). Please refer to subsection 6.5.5 – ATV and Snowmobile Use for further information on their usage.

6.4.3 Commercial fur trapping

Registered Trapline SU-64 encompasses the boundary of this conservation reserve. This registered trapline area is currently allocated to a head trapper. If a head trapper surrenders a registered trapline, or the head trapper’s privileges are revoked, the registered trapline may be transferred to another trapper following established allocation procedures. If the registered trapline is not transferred in due course, or remains unallocated for a significant period of time, reallocation of the trapline may occur following applicable district screening processes. Any proposed new trails for the purposes of commercial fur trapping are subject to the Test of Compatibility (Appendix D) and to screening under the Environmental Assessment Act (e.g., the Class Environmental Assessment (EA) for Provincial Parks and Conservation Reserves). Please refer to subsection 6.3.1b – Trails for further information on the establishment and maintenance of new trails and subsection 6.5.5 – ATV and Snowmobile Use for further information on their usage.

No licensed trap cabins currently exist within Eden Township Forest Conservation Reserve. The establishment of new trap cabins will not be permitted.

6.4.4 Bear management areas

One Bear Management Area (BMA), SU-42-009 is associated with this conservation reserve.

The policies regarding BMA's (OMNR 2003a) states that the issuance of Licences to Provide Bear Hunting Services will be allowed where areas have been licensed or authorized under agreement for the activity since January 1, 1992.

Any proposed new trails for the purposes of bear hunting are subject to the Test of Compatibility (Appendix D) and to screening under the Environmental Assessment Act (e.g., the Class Environmental Assessment (EA) for Provincial Parks and Conservation Reserves). Please refer to subsection 6.3.1b – Trails for further information on the establishment and maintenance of new trails and subsection 6.5.5 – ATV and Snowmobile Use for further information on their usage.

6.4.5 Commercial food collection

There is currently no existing commercial food harvesting venture within the conservation reserve. Any new ventures requiring permits from the Ministry of Natural Resources will be subject to the Test of Compatibility (Appendix D) and to screening under the Environmental Assessment Act (e.g., the Class Environmental Assessment (EA) for Provincial Parks and Conservation Reserves).

6.4.6 Commercial non-timber forest products

Currently, there is no explicit policy direction towards the commercial harvesting of non-timber forest products. New ventures may be considered subject to the Test of Compatibility (Appendix D) and to screening under the Environmental Assessment Act (e.g., the Class Environmental Assessment (EA) for Provincial Parks and Conservation Reserves). Such ventures should be discouraged within the conservation reserve wherever possible, as they do not necessarily coincide with the intent of protecting the area as a conservation reserve.

6.4.7 Outpost camps/main base lodges

There are currently no existing authorized outpost camps or main base lodges within the conservation reserve. New outpost camps and main base lodges may be considered through planning and will be subject to the Test of Compatibility (Appendix D) and to screening under the Environmental Assessment Act (e.g., the Class Environmental Assessment (EA) for Provincial Parks and Conservation Reserves). The form of land tenure for these new uses will remain as a land use permit or lease. Sale of Crown land for new outpost camps or mainbase lodges will not be permitted.

6.5 Non-commercial activities

6.5.1 Nature appreciation/low-impact recreation activities

Off-trail hiking, cross-country skiing, snow-shoeing, and other non-motorized activities will be permitted within this conservation reserve. However, should the impact of these activities degrade the landscape, the Ministry of Natural Resources will re-evaluate these permitted uses and decide upon a new strategy for this site. New trails to support these activities may be considered. Please refer to subsection 6.3.1b- Trails for more details related to trail development.

6.5.2 Camping

There are no maintained campsites or campgrounds within this conservation reserve. Crown land camping policies apply, unless significant adverse effects on protected values necessitate further planning and management for this activity. Existing traditional campsites should be used to avoid disturbance of new areas within the conservation reserve.

6.5.3 Non-commercial consumptive resource use

Cutting of trees for non-commercial purposes may be authorized by the local Ministry of Natural Resources, subject to review and determination of the impact that such cutting would have on the values identified in section 5.0 – State of the Resource. These permits are intended to cover fuelwood, dock stringers, and other occasional small-scale uses. Such permits are intended only for leaseholders, Land Use Permit holders, cottagers and other property owners within the conservation reserve who do not have road access to their property and who do not have an alternate wood source outside of the conservation reserve. Property owners adjacent to the conservation reserve will not be issued permits for areas within the protected area. No stakeholders eligible for non-commercial consumptive resource use permits currently exist within the Eden Township Forest Conservation Reserve.

Non-commercial harvesting of non-timber forest products such as berries and mushrooms can occur provided the values of the site, identified in section 5.0- State of the Resource, are not jeopardized.

6.5.4 Hunting and fishing

In conjunction with current hunting regulations (Wildlife Management Unit 42), hunting is permitted to continue within the conservation reserve. Please see subsection 6.5.5- ATV and Snowmobile Use on the direct retrieval of large game and to subsection 6.3.1b (Trails) for information on the construction of new trails or the maintenance of existing trails.

Recreational fishing is also permitted to continue in compliance with current fishing regulations.

6.5.5 ATV and snowmobile use

An authorized snowmobile trail, Ontario Federation of Snowmobile Clubs trail C108D, has been identified within the site. Please refer to subsection 6.3.1b- Trails for more information on trails. In general, off-trail use of ATVs and snowmobiles is not permitted; however, in some cases, off-trail use is permitted for licensed trappers to access their traplines, for licensed bait harvest operators to conduct bait harvest operations and for use in bear management areas (BMA's). Hunters are also allowed off-trail ATV and snowmobile use for the direct retrieval of large game. In all these cases, any formal intensive off-trail use is discouraged. Should the impact of off-trail ATV and snowmobile use degrade the landscape; the Ministry of Natural Resources will re-evaluate these permitted uses and determine a new strategy.

6.6 Resource management activities

Resource management activities refer to those tools used to protect and enhance the values of this conservation reserve. Some management activities may require the use of intrusive techniques. Under normal circumstances, some of these techniques would not be permitted to occur in the conservation reserve; however, if they are found to be necessary, they may be applied under controlled conditions, to achieve a desired result. Infrastructure such as roads, trails and buildings may need to be constructed to support activities such as prescribed burns, forest regeneration, wildfire control, and insect and disease control. Activities described in this section will be deemed acceptable if the ultimate outcome is in compliance with the management intent for this conservation reserve.

6.6.1 Insect and disease control

This conservation reserve will be maintained in as natural a state as possible. Insect and disease control measures should only be considered if the identified values of the conservation reserve or adjacent forest values on Crown land are significantly threatened. If such measures are proposed, they will be subject to screening under the Environmental Assessment Act (e.g., the Class Environmental Assessment (EA) for Provincial Parks and Conservation Reserves).

6.6.2 Exotic and/or invasive species

The management intent of the conservation reserve is to maintain the site in as natural state as possible. The deliberate introduction of exotic and/or invasive species will not be permitted. If the key values of the site are threatened, new management strategies to control exotic/invasive species may be considered and will be subject to screening under the Environmental Assessment Act (e.g., the Class Environmental Assessment (EA) for Provincial Parks and Conservation Reserves).

6.6.3 Species at Risk management

Any species identified within the conservation reserve that is considered to be either endangered or threatened (as designated by either the national Committee on the Status of Endangered Wildlife in Canada, COSEWIC, or the Committee on the Status of Species at Risk in Ontario, COSSARO) will be given protection under the Fish and Wildlife Conservation Act (1997, S.O. 1997, c.41), the Endangered Species Act (R.S.O 1990, c.E15) and/or the federal Species at Risk Act (June 2003). Recovery plans, consisting of both a recovery strategy and a recovery action plan, prepared for nationally endangered and threatened species under the Accord for the Protection of Species at Risk will be implemented within the conservation reserve if deemed necessary by the Ontario Ministry of Natural Resources and/or the Government of Canada.

6.6.4 Fish and wildlife management

New fish and wildlife management activities (e.g., fish stocking, habitat enhancement/ rehabilitation, population control) may be considered but will be subject to screening under the Environmental Assessment Act (e.g., the Class Environmental Assessment (EA) for Provincial Parks and Conservation Reserves). Existing previously approved fish and wildlife management activities will be permitted to continue but may be subject to screening under the Test of Compatibility (Appendix D) thru the Environmental Assessment Act.

6.6.5 Vegetation management

New vegetation management activities (e.g., the restoration of natural environments) may be considered but will be subject to screening under the Environmental Assessment Act (e.g., the Class Environmental Assessment (EA) for Provincial Parks and Conservation Reserves). Such activities may also require the development of a separate vegetation management plan. Specific management prescriptions, as outlined by the new management plan, must be either referenced within this SCI or attached as an amendment to this document.

6.6.6 Fire Management

The Ministry of Natural Resources recognizes fire as an essential process fundamental to the ecological integrity of conservation reserves. In accordance with existing conservation reserve policy and the Forest Fire Management Strategy for Ontario, forest fire protection will be carried out as on surrounding lands.

Whenever feasible, the Ministry of Natural Resources' fire program will endeavour to use "light on the land" techniques, which do not unduly disturb the landscape, in this conservation reserve. Examples of light on the land techniques may include limiting the use of heavy equipment or limiting the number of trees felled during fire response efforts.

Opportunities for prescribed burning to achieve ecological or resource management objectives may be considered but will be subject to screening under the Environmental Assessment Act (e.g., the Class Environmental Assessment (EA) for Provincial Parks and Conservation Reserves). Such activities may also require the development of a separate vegetation management plan developed in accordance with the Ministry of Natural Resources Prescribed Burn Planning Manual (OMNR 1997b).

6.6.7 Forest Renewal

Forest renewal is an activity associated with commercial timber harvest and with vegetation restoration projects involving tree species. Such practices would only be considered if the area within the conservation reserve had been recently cut prior to becoming regulated or following approval of vegetation management activities as outlined in subsection 6.6.5-Vegetation Management.

Forest loss within the conservation reserve due to wind (i.e., blowdown), fire or insect damage will not be considered for forest renewal – such areas will be left to regenerate naturally. Should unauthorized forest harvest occur within the boundaries of the conservation reserve, forest renewal will be considered.

Any possible renewal project will be reviewed using the Test of Compatibility (Appendix D) and the Environmental Assessment Act (e.g., the Class Environmental Assessment (EA) for Provincial Parks and Conservation Reserves) and would be carried out to replicate natural conditions as much as possible.

6.7 Research

Scientific research by qualified individuals or institutions is encouraged, especially if the research contributes to a better understanding of the natural and cultural values protected by this conservation reserve or if it advances the protection, planning and management of these values. The District Planner, Sudbury District should be contacted for information on research and/or monitoring opportunities within this conservation reserve. Proposals to conduct research should be directed to the Sudbury Area Supervisor, Sudbury District and will be subject to the Test of Compatibility (Appendix D) and relevant Ministry of Natural Resources' policies, procedures and conditions, as well as any applicable Environmental Assessment Act (R.S.O. 1990, Chapter E.18) requirements. Any site that is disturbed during research activities is to be rehabilitated as closely as possible to its original condition. Collecting may only be permitted as part of an authorized research project and may be subject to appropriate permits and conditions.

Existing research and monitoring activities currently occurring within the conservation reserve are permitted to continue, but may be subject to the Test of Compatibility (Appendix D) should detrimental impacts to the values protected by the conservation reserve be detected. No existing research activities have been identified within the Eden Township Forest Conservation Reserve.

7.0 Recommendations

It is recognized that not all features or uses occurring within the Eden Township Forest Conservation Reserve have been identified during the current planning process. This section outlines future activities which might be conducted to ensure that features of the site are protected or to better develop our understanding of the natural features protected by this conservation reserve. Table 3 highlights future needs and considerations for Eden Township Forest Conservation Reserve.

Table 3: Future needs and considerations for Eden Township Forest Conservation Reserve.

Future Needs/ ConsiderationsDetails
Detailed Life Science InventoryA gap analysis of the site should be completed using provincial data sets. This analysis should be used to review the landforms/vegetation information presented in this SCI and the life science checksheet to determine more fully the site’s significance and contribution to the parks and protected areas program.
Key values and sensitive areasA more detailed analysis of the key values and sensitive areas within the conservation reserve could be completed.
VerificationEfforts could be made to locate and GPS the use of any trails or developments and to ensure that off trail use is not impacting sensitive features.
Public EducationEducate the public about the key values in this site and how their activities may impact sensitive features within the conservation reserve (e.g. ATV use in wetland areas, fuelwood cutting).
Signage/Boundary MarkingImportant access points of the conservation reserve (e.g. Lakes End Road) could be marked to help protect the site from adjacent land use activities.
HuntingThrough the public consultation process, a few individuals identified they wanted a ban implemented on hunting in the conservation reserve. This issue may warrant further study and review.

8.1 Monitoring

Periodic monitoring of human activities and/or their impacts within this conservation reserve will be conducted. The Sudbury Area Supervisor and the Sudbury District Enforcement Supervisor will oversee these activities.

Approved inventory, monitoring and/or assessment activities that are compatible with protection objectives are encouraged. Any area that is disturbed during such monitoring activities must be rehabilitated to restore the affected area as closely as possible to its original condition. If at any time human activities are deemed to be negatively impacting the protected features, the activities will be reviewed and measures taken to mitigate any disturbance.

8.2 Marketing

No active marketing of this conservation reserve is anticipated.

8.3 Review and revisions

The Eden Township Forest Conservation Reserve SCI will be reviewed every five years by the District Planner, Sudbury District to confirm and update the information in this document. Revisions to this document will be subject to requirements as specified in the Environmental Assessment Act (R.S.O. 1990, Chapter E.18). If changes in management direction are needed at any time, the significance of the changes will be evaluated. Minor amendments to the plan that do not alter the overall protection objectives may be considered and approved by the Area Supervisor without further public consultation. All minor amendments to the SCI will be documented in Appendix E. In assessing major amendments, the need for a more detailed Resource Management Plan (RMP) will first be considered. Where a RMP is not considered necessary or feasible, a major amendment to management direction may be considered with public consultation. Major amendments will be recommended by the District Manager and approved by the Regional Director, and will follow the appropriate guidelines (OMNR 2001b).

9.0 References

City of Greater Sudbury. Lake Water Quality: Long Lake [Accessed Sept 21, 2004]. Available online at: http://www.greatersudbury.ca.

Cudmore, W., Copeland, C., and Longyear, S. 2004. Eden Township Forest Conservation Reserve (C157) Natural Heritage Area - Life Science Checksheet. Unpublished Information. Ontario Ministry of Natural Resources.

Crins, W.J. and Uhlig, P.W.C. 2000. Ecoregions of Ontario: Modification to Angus Hills' Site Regions and Site Districts – Revisions and Rationale.

Hills, G. A. 1959. A Ready Reference for the Description of the Land of Ontario and its Productivity. Preliminary Report. Ontario Department of Lands and Forests. Maple. Ontario.

Jackson, M. 2004 Recreation Resource Inventory Checksheet for C157 Eden Township Forest Conservation Reserve. Unpublished Information. Ontario Ministry of Natural Resources.

Kristjansson, R.J. 2004. Earth Science Inventory Checklist for C157 Eden Township Forest Conservation Reserve. Unpublished Information. Ontario Ministry of Natural Resources.

Ministry of Citizenship, Culture and Recreation. 1997. Conserving a Future for Our Past: Archaeology Land Use Planning and Development in Ontario, Section 3.

Ontario Ministry of Natural Resources. 1997a. Conservation Reserves Policy PL 3.03.05.

Ontario Ministry of Natural Resources. 1997b. Prescribed Burn Planning Manual. AFFMB Publication No. 313. Ontario Ministry of Natural Resources.

Ontario Ministry of Natural Resources. 1999. Ontario’s Living Legacy Land Use Strategy. Queen’s Printer for Ontario, Ontario, Canada.

Ontario Ministry of Natural Resources. 2000. Conservation Reserve Policy-As Amended by the

Ontario Living Legacy Land Use Strategy. Unpublished document. September 2000.

Ontario Ministry of Natural Resources. 2001a. Forest Information Manual. Queen’s Printer for Ontario: Toronto, Ontario.

Ontario Ministry of Natural Resources. 2001b. Procedures for the Amendment of Ministry of Natural Resources Land Use Direction. Ontario Ministry of Natural Resources.

Ontario Ministry of Natural Resources. 2002. Buildings for Bait Harvesting Management. Public Lands Act, PL 3.03.08.

Ontario Ministry Natural of Resources. 2003a. Direction for Commercial Resource Use Activities in Provincial Parks and Conservation Reserves. June 2003.

Ontario Ministry of Natural Resources. 2003b. A Class Environmental Assessment for Provincial Parks and Conservation Reserves. Queen’s Printer for Ontario, Ontario, Canada. 116 pp.

Ontario Ministry of Natural Resources. 2004. Crown Land Use Atlas. [Accessed: September 15, 2004] www.ontarioslivinglegacy.com/crownlanduseatlas/index.html (link no longer active)

Rowe, J.S. 1972. Forest regions of Canada. Dept. of Fisheries and the Environment. Canadian Forestry Service. Publication No. 1300. 172 pp.

R.S.O. 1990, Chapter E.15. Endangered Species Act. [Accessed: September 1, 2004], /laws/statute/07e06

R.S.O. 1990, Chapter E.18. Environmental Assessment Act. [Accessed: September 15, 2003] /laws/statute/90e18

R.S.O. 1990, Chapter M.14. Mining Act. [Accessed: September 15, 2003] /laws/statute/90m14

R.S.O. 1997, Chapter 41. Fish and Wildlife Conservation Act. [Accessed: September 1, 2004]. /laws/statute/97f41

Thompson, J. 2001. Northeast Region Guidelines on the Planning Process for Conservation Reserves: Statements of Conservation Interest and Resource Management Plan. Unpublished Information. Ontario Ministry of Natural Resources.

Thompson, J. and Noordhof, J. 2003. Edit Model for N.E. Region Life Science Checksheets. Internal Report. Ontario Ministry of Natural Resources.

Uhlig, P., A. Harris, G. Craig, C. Bowling, B. Chambers, B. Naylor and G. Beemer. 2001. Old Growth Forest Definitions for Ontario. Ontario Ministry of Natural Resources, Queen’s Printer for Ontario, Toronto. ON. 27 p.

10.0 Appendices

Appendix A: Eden Township Forest Conservation Reserve maps

Map 1: Recreational Values of Eden Township Forest Conservation Reserve

Map of Recreational Values of Eden Township Forest Conservation Reserve

Enlarge Map 1: Recreational Values of Eden Township Forest Conservation Reserve

Map 2: Landforms in Eden Township Forest Conservation Reserve

Map shows Landforms in Eden Township Forest Conservation Reserve

Map 3: Forest Communities within Eden Township Forest Conservation Reserve

Map shows Forest Communities within Eden Township Forest Conservation Reserve

Map 4: Wetlands within Eden Township Forest Conservation Reserve

Map shows Wetlands within Eden Township Forest Conservation Reserve

Appendix B: Eden Township Forest Conservation Reserve photos

Photo 1: Large white birch along access trail.
(Photo taken by Joey Young, OMNR, Aug. 5, 2004)

Photo shows Large white birch along access trail.

Photo 2: Large poplar along recreation trail.
(Photo taken by Joey Young, OMNR, Aug. 5, 2004)

Photo shows Large poplar along recreation trail.

Photo 3: Access trail (left) joins recreation trail (Broder Dill Snowmobile Trail #4).
(Photo taken by Joey Young, OMNR, Aug. 5, 2004))

Photo shows Access trail (left) joins recreation trail (Broder Dill Snowmobile Trail #4).

Photo 4: Red pine-white birch mixed forest stand along Lakes End Road.
(Photo taken by Joey Young, OMNR, Aug. 5, 2004)

Photo shows Red pine-white birch mixed forest stand along Lakes End Road.

Photo 5: Red pine-cedar stand in northeast section of site, along driveway to private land.
(Photo taken by Joey Young, OMNR, Aug. 5, 2004)

Photo shows Red pine-cedar stand in northeast section of site, along driveway to private land.

Photo 6: View of meadow marsh along eastern boundary from recreation trail.
(Photo taken by Joey Young, OMNR, Aug. 5, 2004)

Photo shows View of meadow marsh along eastern boundary from recreation trail.

Appendix C: Summary of permitted uses

The following Policy Report was obtained from the Crown Land Use Policy Atlas website during completion of this SCI (fall 2004). Changes may have been made to this policy report since that time. For the most recent version of this policy report, please refer to the Crown Land Use Policy Atlas on the internet at /page/crown-land-use-policy-atlas or contact your local Ministry of Natural Resources office.

Crown Land Use Policy Atlas - Policy Report

Updated: June 29, 2004
Eden township forest

Identification:

ID: C157
Area Name: Eden Township Forest
Area (ha): 145
Designation: Conservation Reserve (Ontario’s Living Legacy)
MNR District(s): Sudbury

Description:

This conservation reserve located in Long Lake (lake trout lake), in Site District 5E-4 protects a red pine and cedar forest on a landscape of low hills. This forest provides the best example of this landform/vegetation complex in the area.

Eden Township Forest was regulated as a conservation reserve on December 7, 2002.

Land use intent:

The land use intent of this area will be to protect the natural heritage values of the red pine and cedar forest.

Management of this area is also governed by the general policies contained in the Land Use Strategy (1999).

Management direction:

Those uses and management activities not listed in the following table are governed by existing conservation reserve policy Over time the management direction will be elaborated in a Statement of Conservation Interest or Resource Management Plan. Any new uses, and commercial activities associated with conservation reserves, will be considered on a case by case basis, and they must pass a test of compatibility to be acceptable Compatibility is normally determined through a planning process.

Commercial activities

ActivityPermittedGuidelines
Aggregate ExtractionNoN/A
Bait Fishing Existing:YesExisting use permitted to continue, unless there are significant demonstrated conflicts.
Bait Fishing New:MaybeNew operations can be considered, subject to the "test of compatibility"
Commercial Fishing Existing:YesExisting use permitted to continue, unless there are significant demonstrated conflicts.
Commercial Fishing New:MaybeNew operations can be considered, subject to the "test of compatibility".
Commercial Fur
Harvesting Existing:
YesExisting use permitted to continue, unless there are significant demonstrated conflicts. Existing trap cabins can continue; new cabins are not permitted.
Commercial Fdur
Harvesting New:
MaybeNew operations can be considered, subject to the "test of compatibility".
Commercial Hydro DevelopmentNoN/A
Commercial Timber
Harvest
NoN/A
Commercial Tourism Existing:YesExisting authorized facilities can continue, unless there are significant demonstrated conflicts.
Commercial Tourism New:MaybeNew tourism facilities can be considered during the planning for an individual reserve.
Bear Hunting by Non­ residents (guided) Existing:YesExisting authorized operations permitted to continue.
Bear Hunting by Non­ residents (guided) New:NoNew operations not permitted.
Outfitting Services Existing:YesExisting authorized operations permitted to continue.
Outfitting Services New:MaybeNew operations can be considered during the planning for an individual reserve.
Outfitting Services Existing:YesExisting authorized operations permitted to continue.
Outfitting Services New:MaybeNew operations can be considered during the planning for an individual reserve.
Outpost Camps Existing:YesExisting authorized facilities permitted to continue.
Outpost Camps New:MaybeNew facilities can be considered during the planning for an individual reserve.
Resorts/lodges Existing:YesExisting authorized facilities permitted to continue.
Resorts/lodges New:MaybeNew facilities can be considered during the planning for an individual reserve.
Energy Transmission and Communications Corridors Existing:YesThese facilities should avoid conservation reserve lands wherever possible.
Energy Transmission and Communications Corridors New:NoN/A
Food Harvesting (Commercial) Existing:MaybeN/A
Food Harvesting (Commercial) New:MaybeN/A
Mineral Exploration and DevelopmentNoN/A
Peat ExtractionNoN/A
Wild Rice Harvesting Existing:YesN/A
Wild Rice Harvesting New:MaybeN/A

Land and resource management activities

ActivityPermittedGuidelines
Crown Land Disposition Private Use:MaybeSale of lands is not permitted, except for minor dispositions in support of existing uses (e.g. reconstruction of a septic system). Renewals of existing leases and land use permits are permitted. Requests for transfer of tenure will be considered in the context of the Statement of Conservation Interest or Resource Management Plan.
Crown Land Disposition Commercial Use:MaybeNew leases or land use permits permitted for approved activities. Tourism facilities can apply to upgrade tenure from LUP to lease.
Fire SuppressionYesFire suppression policies are similar to adjacent Crown lands, unless alternative fire policies have been developed through a planning process.
Fish Habitat ManagementMaybeN/A
Fish StockingMaybeExisting authorized operations permitted to continue. New operations not permitted.
Inventory/disease SuppersionMaybeN/A
Inventory/MonitoringMaybeN/A
Prescribed Burning Roads (Resource Access) Existing:YesExisting roads can continue to be used. Continued use will include maintenance and may include future upgrading.
Prescribed Burning Roads (Resource Access) New:MaybeNew roads for resource extraction will not be permitted, with the exception of necessary access to existing forest reserves for mineral exploration and development.
Vegetation ManagementMaybeConservation Reserves policy indicates that Featured Species Management and Natural Systems Management may be permitted. Vegetation management can be considered in a planning process.
Wildlife Population ManagementMaybeN/A

Science, education and heritage appreciation

ActivityPermittedGuidelines
CollectingNoN/A
Historical AppreciationYesN/A
Nature AppreciationYesN/A
Photography and PaintingYesN/A
ResearchYesN/A
Wildlife ViewingYesN/A

Recreation activities and facilities

ActivityPermittedGuidelines
All Terrain Vehicle Use On Trails:YesExisting use permitted to continue where it does not adversely affect the values being protected. ATV use off trails is not permitted except for direct retrieval of game.
All Terrain Vehicle Use Off Trails:NoN/A
CampgroundsMaybeN/A
Food GatheringYesN/A
Horseback Riding(trail)YesExisting use on trails permitted.
HuntingYesN/A
Mountain Bike UseYesExisting use on trails permitted.
Motor Boat Use Commercial:YesN/A
Motor Boat Use Private:YesN/A
Non-motorized Recreation TravelYesN/A
Private Recreation Camps (Hunt Camps) Existing:YesN/A
Private Recreation Camps (Hunt Camps) New:NoExisting camps permitted to continue, and may be eligible for enhanced tenure, but not purchase of land.
Rock ClimbingMaybeN/A
Snowmobiling On Trails:YesExisting use permitted to continue where it does not adversely affect the values being protected.
Snowmobiling Off Trails:MaybeSnowmobile use off trails is not permitted, except that snowmobiles may be used for direct retrieval of game.
Sport FishingYesN/A
Sport Fishing Trail Development Existing:YesDevelopment of trails for a variety of activities (e.g. hiking, cross-country skiin, cycling, horseback riding, snowmobiling) can be considered as part of planning for an Individual reserve.
Sport Fishing Trail Development New:MaybeN/A

Note: The policies outlinedin this table do not supersede any Aboriginalor treaty rights that may exist, or other legal obligations.

Management of this conservation reserve is carried out within the context of Conservation Reserve policy as amended by the policies for new conservation reserves outlined in the Ontario’s Living Legacy Land Use Strategy

Source of direction:

Ontario’s Living Legacy Land Use Strategy (1999) Conservation Reserves Policy (1997)

Explanation of edits:

Area calculation has been edited based on current mapping Area calculations are preliminary until public consultation on boundaries has been completed and the area has been regulated.

Appendix D: Test of Compatibility

The Conservation Reserve policy provides broad direction with regard to the permitted uses. The policy provides only an indication of the variety of uses that will be considered acceptable in conservation reserves. Any new uses, and commercial activities associated with them, will be considered on a case by case basis, and, subject to the following test of compatibility. To ensure a standard screening process is followed, reviews of all current and new activities will be subject to the screening criteria as specified by the Environmental Assessment Act (R.S.O. 1900, Chapter E.18).

The following outlines the two steps involved in performing a Test of Compatibility. An assessment of current activities would only follow step two, which focuses on the impacts. An assessment of any new activity would consider the impact of the activity and its conformity to the SCI/RMP.

  1. Conformity to SCI/RMP: SCI describe values for which an area has been set aside and the range of appropriate uses that will be permitted in the area. SCI may also speak to the acceptability of other 'new' uses currently not occurring in the area.

    The first 'test' is: "do proposed new land uses and/or commercial activities conform to the direction of the SCI/RMP for the conservation reserve? Would the new use(s) depart from the spirit of appropriate indicator land uses in the SCI/RMP?"

  2. Impact Assessment: If the proposed use(s) pass test 1 it is important to determine their impact on the area before they are approved. This should include the following:

    • Impact on natural heritage values: "will the new use(s) impact any natural values in the area? If so how and to what degree? Is it tolerable?"
    • Impact on cultural values: "will the new use(s) impact an historical or archaeological values in the area?"
    • Impact on research activities: "will the new use(s) affect research activities in the area?" Impact on current uses: "will the new use(s) have any negative impact on the array of current uses?"
    • Impact on area administration: "will the new use(s) increase administrative costs and/or complexity?" (For example, the cost of area monitoring, security and enforcement).
    • Impact on accommodating the use outside the conservation reserve: "Could the use(s) be accommodated as well or better outside the conservation reserve?"
    • Impact on socio-economics of the area: "will the new use(s) affect the community(ies) surrounding the area in a positive or negative way?" (For example, will the new use make an area less remote thereby affecting a local tourism industry that is dependent on the area’s remoteness for its appeal?"
    • Impact on area accessibility: "does the new use(s) give someone exclusive rights to the area or a portion of the area to the exclusion of other existing uses?"

Appendix E: Amendments to the SCI


1Ecodistricts are areas characterized by physiographic (landform) similarities, and by the successional trends exhibited by the predominant vegetation types on those physiographic features, see section 5.0-State of the Resource (Hills 1959; Crins and Uhlig 2000).

2Stocking is defined as follows: a qualitative measure of the density of tree cover in a forest stand. Stocking represents the density of forest stems based on average age, height, and the working group (the dominant tree species) in a forest stand. (OMNR 2001a).

3Disturbance rating is based on the amount of conservation reserve area currently under some form of known disturbance: >20%, high; 10-20%, medium; < 10%, low (Cudmore and Longyear 2004).

4Diversity rating is based on the size of the protected area versus the number of landforms: vegetation (SFU/HU) combinations. For conservation reserves between 500 to 2000 ha in size, >30 L:V combinations is considered to have high diversity, >20 L:V combinations is considered to have medium diversity, and < 20 L:V combinations is considered to have low diversity (Thompson and Noordhof 2003)

55 Evenness of the site defined as strongly skewed (top 3 communities capture >=60% of the site in area), moderately skewed (30-59%) or slightly skewed to even (< 30%).