Body: Council Type: By-law Meeting: Regular Date: 2013 Collection: By-laws Municipality: South Frontenac
[View Document (PDF)](/docs/south-frontenac/By-laws/2013 By-laws/2013-07 - Site Plan Agreement 1324789 Ontario Inc.pdf)
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TOWNSHIP OF SOUTH FRONTENAC BY-LAW NUMBER 2013-07
BEINGABY:LAWTOAUTHORIZ]E THE MAYOR AND THE CLERK TO EXECUTE A^REVISED SITE PLAN AGREEMENT BETWEEN~THE
CORPORATIONOF TIffi TOWNSHIP OF SOUTH FRONTENAC-AND 1324789 ONTARIO INC. AND JACO INVESTMENTS LTD.
WHEREAS a revised Site Plan Agreement has been prepared to the sadsfaction of the Township of South Frontenac and signed by the proponent;
NOW-THEREFORE THE CORPORATION OF THE TOWNSHIP OF SOUTH FRONTENAC BY ITS COUNCIL, HEREBY ENACTS AS FOLLOWS:
THAT the Mayor and the Clerk are hereby authorized to execute a revised Site Plan Ag-eement between the Corporation of the Township of South Frontenacand 1324789 Ontario Inc. and JACO Investments Ltd., a copy of which is attached hereto and forms part of this by-law.
THAT this By-law and Agreement shall be registered on title of the property
described as Part Lots 23 & 24, Concessions VI & VII, Loughborough District, Township of South Frontenac.
- THIS BY-LAW shall come into force and effect in accordance with section 41 of
the Planning Act 1990, either upon the date of passage or as otiierwise provided by the said section 41.
Dated at the Township of South Frontenac this fifth day of February, 2013. Read a first and second time this fifth day of February, 2013.
Read a third time and finally passed this fifth day of February, 2013. THE CORPORATION OF THE
TOWNS^I^^OUTm.RONTIEMAC Gary Davison, Mayor
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lerk-Administrator
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THIS SITE PLAN AGREEMENT made this day of February, 2013. BETWEEN:
1324789 ONTARIO INC. & JACO INVESTMENTS LTD. heremafter called the “Owner” OF THE FIRST PART
- and -
THE CORPORATION OF THE TOWNSHIP OF SOUTH FRONTENAC hereinafter called the “Municipality” OF THE SECOND PART »..
WHEREAS the Owner is the registered owner in fee simple of certain lands described in Schedule “A”, attached hereto, located in the Township of South Frontenac (the “Owner’s Land”);
AND WHEREAS the Municipality is authorized to enter into this agreement and register it against the title to the Lands pursuant to section 41 of the Planning Act and section 6.17 of the Township of South Frontenac Official Plan;
AND WHEREAS the Municipality has passed by-law No. 2003-75 to designate all of the Township of South Frontenac as a “Site Plan Control Area”; NOW THEREFORE, TMS AGREEMENT WITNESSETH that in consideration of
the mutual covenants and agreements contained herein, the parties agree each with the other as follows:
In this Agreement: a)
“Owner” includes a mortgagee in possession, a tenant in possession pursuant to a leasehold interest, and encwnbancer in possession and may mean more than one Owner specified in the Certificate of ownership.
The Owner covenants that the Owner is the Owner m fee simple of the Owner’s land.
The obligations unposed by this Agreement affect the land described in Schedule “A” hereto and any restrictive covenants expressed herein run with the land and bind successors in title to the said property as well as the successors and assigns of the Owner.
The encumhrancer agrees to satisfy all the obligations imposed pursuant to this document if it should enter into possession of the said land.
- The following schedules are attached to and form part of this agreement and no new building, structure or other facility shall be erected, altered or placed on the said land except in accordance with the attached schedules which consist of:
A. Legal Description of Lands B.
Site Plan
C. Enymmmental Site Evaluation Report Dated June, 2011 prepared by
^cologicalServices^reconunendationreport dated December-8-,201 from the Cataraqui Region Conservation Authority
- The Owner shall perfonn all the work and provide all the materials necessary for
construction of all principal and accessory buildings andprivate-sewa-g facilities.
e
- The Owner may construct a single detached dwelling and accessory structures located a minimum of 35 meb-es (115 ft.) from the highwater mark of Loughborough Lake at a location behind an existing nse of land that would
effectively be between the lake and the dwelling providing a barrier to slope runoff from the developed area to the lake generally as shown on Schedule “B”
- The access easement that provides access to the subject property shall be
constructed to minimum- To^ship Standards’ for newprivate-lanes and it shall be recognized that the lane is not subject to any maintenance or other services provided by the Municipality.
- Development of the lot shall be m accordance with the recommendations from the
Environmental Site Evaluation Report and the Cataraqui Region Conservation Authority as attached hereto as Schedule “C”
In the event of a sale of the improved lands, the new Owner will assume full and
complete responsibility for the continuing obligations under this Agreement. The enforcement of this Agreement is the responsibility of the Municipality.
- The Agreement shall be registered against the title of the Lands and the
Municipality shall be entitled to enforce its provisions against the Owner and any and all subsequent owners of the Lands.
- In the event that the Owner fails to install or maintain the facilities covered by this Agreement, then, upon the Chief Building Official or designate, giving seven days written notice by pre-paid registered mail to the Owner, the municipality, through it’s employees, agents or contractors, may, without further notice, enter upon the lands and proceed to supply all materials and to do all the necessary inspections and works in connection with the facilities mcluding the repair or reconstruction of faulty work and the replacement of materials which are not in accordance with plans or specifications and to charge the cost thereof, together with the cost of engineering and any other expenses incurred by the municipality, against the Owner. Such entry and work shall not be deemed as acceptance or assumption of
said facilities nor an assumption by the Municipality of any liability. It is
expressly agreed that the Owner or any person in possession shall not question the cost incurred by the Municipality for labour, materials or any other costs incidental to do the said work and this provision shall be deemed to operate as an effective estoppel in judicial proceedings if such costs are challenged or placed in question. The Owner agrees to permit the Chief Building Official, or agent, to enter onto the Lands at any time to inspect the work. The Municipality may perform any of the required services and collect the cost for the enforcement of
this Agreement against the said Lands from the security.
12. The Owner covenants and agrees that the lands and premises more particularly described in Schedule “A” annexed hereto may only be used for those purposes specified by Zoning Amendment By-law No. 2013-04.
WITNESS the corporate seals of the respective corporate parties hereto, duly affixed under the hands of their respective signing officers, duly authorized in that behalf.
SIGNED, SEALED AND DELIVERED ) In the presence of
THE CORPORATION OF THE TOWNSHIP OF SOUTH FRONTENAC
Mayor
Clerk
SCHEDULEMAW LEGAL DESCRIPTION OF LANDS
Part Plan 13R-; Part of Lot 23, Concession VI, Loughborough District, Township of South Frontenac
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SCHEDULE_“C_M ENVIRONMENTAL SITE EVALUATION REPORT &
REPORT FROM CARARAQUI REGION CONSERVATION AUTHORITY
CATARAQUI REGION CONSERVATION AUTHORITY 1641 Perth Road, RO. Box 160 Glenbumle, Ontario KOH.1SO Phone; (613) 546-4228 Toll-free (613 area code): 1-877-956-CRCA
.1
Fax: (613) 547-64/4 E-mail: crca@cataraquiregion.on.ca
Websites; www.cleanwatercataraqui.ca & www.cataraquiregion.on.ca December 8, 2011
File: SEV/FRS/142/20U SEV/FRS/143/2011 SEV/FRS/144/2011
Sent by Email
Anne Levac, Planning Assistant Township of South Frontenac P.O. Box 100
Sydenham. ON KOH 2TO Fax:613-376-6657
Dear Ms. Levac, r t
Re: Applications for Consent to Sever S-54-11-L, S-55-U-L, S-56-11-L (Beck) Part Lot 23/24, Concession 6/7; Loughborough District New lane off of North Shore Road
Loughborough Lake Complex PSW and Loughborough Lake Swamp ANSI Long Bay / East Basin of Loughborough Lake
Further to our letter dated November 29, 2011, staff of the Cataraqui Region Conservation Authority (CRCA) have received a response dated December 2, 2011 from Ecological Services and a revised Environmental Impact Assessment (EIA), dated December 201 1.
Staff are generally satisfied with the responses, however, continue to encourage a 40 m setback .1
from the shoreline for future development. With respect to response to Comment 3 in our previous letter, there appears to be a discrepancy between the EIA findings and fhe sketch by Clancy & Hopkins. dated October 30, 2011, that is included as Figure 1 of the EIA. The EIA identifies that the closest distance between the proposed laneway and the Provincially Significant Wetland (PSW) wiU be 60 m. Based on the scale provided on Figure 1, it appears that the edge of the proposed laneway would be located approximately 30 m from the edge of the PSW at its closest point in the northern portion of the property. As such staff recommend that the sketch by Clancy & Hopkins be updated to reflect the EJA*s findings. As recommended by the EtA consultant, a road should not be allowed closer fhan 30 m from the PSW boundary. Staff have no objection to the approval of applications S-54-11-L, S-55-11-L, S-56-11-L based on the findings of the EIA and provitled that the following conditions of approval are required: .
That the sketch by Clancy & Hopkins be updated to reflect the ElA.’s findings regardmg the location of the proposed laneway with respect to the Provincially Significant Wetland (i.e. closest distance to the proposed road would be 60 m). That the subject lands be re-zoned to an appropriate residential zone that requires that all future buildings and structures to be located a minimum- of 40 m from the shorelme of M ember of
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Ms. AnneLevac (S-54-11-L, S-55-I1-L, S-56-11-L) December 8,2011
Loughborough Lake, and all septic fields to be located at least 60 m from the shoreline of Loughborough Lake on the lots to be severed and retained. .
That the 30 m setback adjacent to Loughborou^i Lake or the Provincially Significant Wetland be maintained in a natural state. A natural state means no clear cutting or importing large amounts of fill in order to have mowed lawns.
.
That no development takes place within any steep slope located above the Provincially Significant Wetland in order to minimize sediment and erosion impacts.
.
That development on Lot 3 (application (S-56-11-L) occur tlirough site plan control for
which review by the CRCA will be required. A survey by an Ontario Land Surveyor (OLS) shall be completed prior to the development of Lot 3 demonstratmg that there is a
.
suitable buildmg envelope outside of the required setbacks of 40 m from the shoreline of Loughborough Lake, 30 m from the “narrow wetland extension” identified in the EIA, and 15 m from the “poor drainage area that contains wetland vegetation” identified in the EIA. The septic field is to be located 60 m from the shoreline and setback 30 m and 15m from the “narrqw wetland extension” and “poor drainage area that contains wetland vegetation” respectively. The proposed laneway and the cul-de-sac at the end of the proposed laneway must also meet the 30 m and 15 m setbacks identified above. That sUt screens and hay bale silt barriers be placed between any construction areas within 30 m of the lake or wetland. They should also be periodically checked to ensure proper functioning. There should be no construction activities closer than 30 m to fish habitat.
.
That permission from the CRCA under Ontario Regulation 148/06: Development, Interference with Wetlands, and Alterations to Shorelines and Watercourses, will be required prior to any development or site alteration (including the placement or removal of fill) within 120 m of any Provincially Significant Wetland, 30 m of other wetlands, or 30 m of the shoreline of Loughborough Lake, and for any in-water works.
It is recommended that a development agreement be used as a tool to ensure that these recommendations are addressed.
If you have any questions, please contact the undersigned at (613) 546-4228 extension 258. or by e-mail at sagarwal@cataraquiregion.on.ca. Please inform this office in writing of any decision made by the Committee of Adjustment with regard to these applications. Yours truly,
oUl^(^M^/ (/-Sukriti Agarwal, AICP Environmental Planner
Attachment: Email correspondence dated December 7, 2011 between Rob Snetsinger, Ecological Services, and Tom Beaubiah. CRCA Biologist.
Page 2 of 2 r-
Sukriti Agarwal From: Sent:
Torn Beaubiah [beaubiah@cataraquiregion.on.ca] Wednesday, December 07, 2011 3:51 PM sagarwal@cataraquiregion.on.ca
To:
Subject:
FW: Johnston Point EIS
See below
Sincerely/ Tom Beaubiah
Biologist r
iraqui Region Conservation Authority
^. ^. Box 160 -1641 Perth Road
Glenburnie, Ontario KOH ISO
Phone: 613-546-4228 ext 240 Fax: 613-547-6474
Webiste: www.cataraauireeion.on.ca *
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From: Rob Snetstnger [mailto:snetsina(S>qu^eQsUt£3] Sent: Wednesday, December 07,2011 11:06 AM To: Tom Beaublah
Subject: Re: Johnston Point EIS Hi Tom,
I don’t think it is possible to accurately portray precise distances with the various figures, which are mostly conceptual. My impression early on (taken from the maps) was that a road there would be problematic It was only after 1 saw the surveyors flagging tape (marking the property boundary) and then doing a pace to the wetland was I reassured about
distances. A road should not be allowed closer than 30 m, and I think the easiest thing at this point is to make that a condition of approval at the site plan level. Rob
On 12/6/20114:54 PM, Tom Beaubiah wrote:
Rob, Thank you for your comments with respect to the EIS for Johnston Point. We are finalizing our comments to the Township and wanted to get clarification on Comment 3. Per your wetland boundary delineation you defined an approximate 60m boundary between the road and the wetland. This representation however did not get incorporated into figure 1 of your report. Our concern was that when scaled out on figure 1 the surveyor has delineated the wetland boundary at approximately 30m. If you can let me know (ec Sukriti) if you will have a chance to comment on that it would be appreciated. Sincerely, 1
Tom Beaubiah
Biologist
Cataraqui Region Conservation Authority P,0. Box 160-1641 Perth Road
Glenburnfe, Ontario KOH ISO Phone: 613-546-4228 ext 240 Fax: 613-547-6474
Weblste: www.cataraautreeion.on.ca
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Environmental Impact Assessment Johnston Point
Prepared by: Ecological Services 3803SydenhamRd.
Elginburg, Ontario KOH 1MO Phone: (613) 376-6916; Fax: (613) 544-0072 E-mail: ecoserv@kos.net
Prepared For:
June 2011
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Environmental Assessment Johaston Point
Table of Contents
Summary
3
Methodology
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5
Ecological Land Classification
5
Regulations
7
Provincial Planning Policy ………………………………. 8 Significant Features
a) Significant Wetlands…………………………. 9 c) Woodlands………………………………………10 e) Significant Wildlife Habitat …»..»»………….ll 0 Fish Habitat……………………………………. 16 Literature Cited …………,………-…………..*………- 16
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Environmental Impact Assessment Johnston Point SUMMARY
This environmental assessment was initiated as a result of a proposal by Gary and Martha Beach for three severances on Johnston Point (Lougborough Lake) and the building of three dwellings and an associated access road (see Figure 1).
Johnston Point is located about 2 m east of Perth Road (Division St) on the north shore of
Loughborough Lake. It is associated with the provincially significant Loughborough Lake Wetland Complex. The point has been used for cattle pasturing, but has been developing back into forest for about 30 years. The environmental constraints discussed include significant wetland, woodlands, significant wildlife habitat, and fish habitat.
For the purposes of the PPS, there will be no negative impacts to any significant natural heritage feature. List ofRecommendations/Mitigation
It is recommended fhat buildings be set back a minimum of 40 m from the edge of Loughborough Lake. Closer distances up to 35 m are possible if it can be shown that the land is sloping away from the lake, resulting in longer flow distances for stormwater. All septic fields will be 60 m from the lake.
In order to minimize sediment and erosion impacts, it is recommended that no development take place within any steep slope located above the provincially significant wetland. The steepest slopes are mainly associated with the swamp at the very end of Long Bay.
It is recommended that a 100 mportion of access road to be located on a moderate
slope, 60 m from the Long Bay swamp, be designed to engineering and approved standards for erosion protection.
- A 15 m setback from the small arm of wetland vegetation associated with the westernmost lot is deemed sufficient. However we still recommend site plan controls
(e.g., building placement) that push for greater distances from this wetfand feature. 5. It is recommended that when the specific building sites are surveyed, a last check for snake hibemacula be undertaken. Ifhibemacula are found, building relocation will have to be undertaken.
- As is normal for any work near fish habitat, silt screens and hay bale silt barriers should be placed between any construction areas withm 30 m of the lake or wetland. 3
They shouldalso be penodically checked to ensure proper functioning. There should be no construction activities closer than 30 m to fish habitat.
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Sketch
of parts of Lots 23 and 24 Concessions 6 and 7
Geographic Township of Loughborough
now Township of South Frontenac County of Frontenac
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Figure 1. Proposed severances and tinaree building lots.
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> V-.w ....'. \< *** ;» . » . *..'. fc' **'.f <.' * F . f* I * * * ».. .^*-. * ^ * * » <» . < *. 1 "Wt ^ 11 i» tf I .^.4^ ^ .^ H II * \ . * v ^\ *» t. » » * * . 24 w% METHODOLOGY: ^.=xs~s,2=^s's'^?s; the field work was conducted by Rob Snetsinger, with assfstance from Chris Grooms: of An aerial flight was also taken m 2010. ECOLOGICAL LAND CLASSIFICAITON Past cattle grazing on the property has strongly influenced its current ecology. Title Ecological Land Classification (ELC) Manual for Southern Ontario (see Lee et al. 1998) provides the basis for the ELC designations that are presented in Figure 3. As can happen with ELC mapping, habitat patches below the 0.5 ha. size threshold are lumped into a larger surrounding type. The ELC map also contams other codes that are not specific ELC designations. Cultural Meadow (CUM): This community type is characterized in the ELC manual as having a tree and shrub cover of less than 25%, and results from and/or is maintained by cultural disturbances (ie., usually farming). This site contams common agricultural grasses mixed with various field forbs such as Goldenrod, Wild Carrot, Asters, and Clovers. CUM communities arc considered to have relatively low ecological value, and thus low potential for significance, because of their young age and high proportion of non-native species. Cultural Thicket (CUT). This community type is characterized in the ELC manual as having a shmb cover of greater than 25%, and here it is dominated by Juniper, Red Cedar, Prickly Ash, and Gray Dogwood, which are commonly found on lands with shallow soils that have been grazed in the past. Younger White Oak, White Ash, and White Pine are also growing amongst the shrubs. There is also evidence that cultural thicket once covered much of Johnston Point in the form of remnant juniper branches. Juniper would be expected in an area with shallow soils and a past history of grazing use. However shrub areas have since given way to younger forest succession. Dry -Fresh Sugar Maple - Ironwood Deciduous Forest Type (FOD5-4). As the name implies, this forest type is dominated by Sugar Maple, with Ironwood being the second most dominant tree. As described in Lee et al (1998), this is a common forest type found on areas with a history of grazing use. The bulk of the trees are in the 30 year age range, although sporadic patches of larger older trees are present. The most common imderstory plant present is Carex pewisylvanica, which is also common in forests with a grazing history. 5 ^t- Mixed Forest (FOM). This forest type is mostly associated with fence lines, slopes, lower elevations next to the wetland, and the adjacent properties. It contains older and larger trees than the FOD5-4 sites. There is no clear dominant but there is an s'r^r-s-jss^'ss^ssss'.^ theunderstory such as Raspberry and perennial forbs (e.g.Buttercup, Canada Anemone, Vetch). Figure 3. ELC designations ofJohnston Point Dry Fresh Cedar Coniferous Forest (FOC2); Dry -Fresh Sugar Maple - Ironwood Deciduous Forest Type (FOD5-4). These areas contained distmct stands ofFOC2 and FOD5-4, but they were too intermixed to be mapped as separate areas. The Cedar component was mostly Red Cedar, but patches of White Cedar also existed. Similar to the FOD5-4 stands, the coniferous stands are common on lands with a grazing history. Both stands contain trees m the 30 year range and it is expected that in time, the deciduous trees will overgrow and push out the coniferous trees. Red Maple Mineral Deciduous Swamp Type (SWD3-1). Red Maple is the dominant canopy trees m these areas, but Silver Maple and Black Ash are also present. The shrub layer contained a diverse mbc of wetland species such as Red Osier Dogwood, Speckled Alder, Myrica Gale, Nannyberry, and Spirea. The^ground cover also was quite diverse with a number of species such as Touch-me-not, Bedstraws, Marsh Marigold, Marsh Fern, Sensitive Fern, and wetland grasses. This is part of the Loughborough Lake Wetland Complex* 6 REGULATIONS Fisheries Act Under Section 35 of the federal Fisheries Act: " no person shall carry on any work or undertaking that results in the harmful alteration, disruption or destruction of fish habitat." There are no plans to work within fish habitat. Species at Risk Act Under Section 32 of the federal Species atRiskAct: "no person shall kill, harm, harass, capture or take an individual of a wildlife species that is listed as an extirpated species, an endangereQ species or a J threatened species." \ if / t Under Section 33 of the federal Species at Risk Act: " no person shall person shall damage or destroy the residence of one or more individuals of a wildlife species that is listed as an endangered species or a threatened species ff Two Buttemut trees were found on the property. An OMNR Buttemut Health Assessment was undertaken and neither tree scored as retainable. An OMNR permit to remove these Buttemuts (if they need to be removed) will be processed. Migratory Birds Convention Act Regulation, 6. Subject to subsection 5(9), no person shall (a) disturb, destroy or take a nest, egg, nest shelter ...of a migratory bird... The development property contains migratory birds and it would be a contravention of the act if these nests were destroyed during construction activities. Infractions can be avoided by working outside of the breeding and nesting periods (generally early April to early August). It is possible to work within the breeding season as long as the site is cleared prior to the nesting period to make it uninhabitable to migratory birds. « 7 *-». n*f PROVINCIAL PLANNING POLICY The focus of this EIA will be to address issues associated with the Provincial Policy Statement (PPS). Issued under Section 3 of the Planning Act, Section 2.1 of the PPS requires that municipalitiesconsider natural heritage features in assessing development proposals. Guidance on the extent of adjacent lands is provided in a Natural Heritage Reference Manual (OMNR 2010). The adjacent land width for significant natural heritage features is 120 m. From the Policy: 2.1.3 Development and site alteration shall not be permitted in: b) significant wetlands in Ecoregions 5E, 6E and 7E; There will be no development within the significant wetland, but there will be development adjacent to significant wetland, t f 2J .4 Development and site alteration shall not be permitted in: b) significant woodlands south and east of the Canadian Shield; The Johnston Point is within the Canadian Shield. Therefore the PPS does not apply for woodlands. Nevertheless, impacts to woodland features and functions are discussed, as they relate to significant wetlands. d) significant wildlife habitat; There will be no development withm significant wildlife habitat, but there will be development adjacent to significant wildlife habitat. 2.1.5: Development and site alteration shall not be permitted in fish habitat except in accordance with provincial and federal requirements. There will be no development within fish habitat, but there will be development adjacent to fish habitat* 2.1.6: Development and site alteration shall not be permitted on adjacent lands to the natural heritage features and areas... unless the ecological function of the adjacent lands has been evaluated and it has been demonstrated that there will be no negative impacts on the natural features or on their ecological functions. 8 Adjacent lands are defined in the PPS: ".. .those lands contiguous to a specific natural heritage feature or area where it is likely that development or site alteration would have a negative impact on the feature or area... w Guidance on the extent of adjacent lands is provided in a Natural Heritage Reference Manual (OMNR 2010), which lists an adjacent land width of 120 m for all significant heritage features. SIGNIFICANT FEATURES a) Significant Wetlands The Louborough Lake wetland complex has evaluated by a crew from the CRCA m 1985 and was determined to be significant, primarily due to its large size and Special Features. It should be noted that all of the species listed as rare in 1985 are now at least S4 or higher, and these species would not be includedmthe scoring. We note in the wetland mapping that Long Bay was not given a wetland community code, which suggests that Long Bay is not wetland. We assume this to be an oversight, as Long Bay does contain a submergent wetland community. The small wetland bays within Johnston's Point were labeled S2, S4 and S27, and all were noted to be dominated by ground cover forms (e.g., perennial herbs), followed by shrub forms. This may have been the case in 1985, but in 2011 these bays were dominated by tree forms (e.g.. Red Maple), with a secondary dominance of shrub forms. In order to address impacts to the wetland with respect to the PPS, we used wetland evaluation to identify key features and functions. We have undertaken more than 100 wetland evaluations and are well qualified to review the steps. The wetland evaluation quantitatively ranks the wetland with a numerical value. If the proposed development were to have a negative impact on the wetland, then this could result in a lower numerical value in the wetland evaluation* Biological Component: This component covers basic structural components that promote biodiversity. The four main categories are Productivity, Biodiversity, Ecosystem Age, and Size, and each of these has several sub-categories. The wetland received a high score m the Biological Component, with the highest score awarded for its large size and the diverse mix of vegetation communities found within its 5.2 km length. Reviewing the Biological Component scoring line by line, we can state with confidence that the score will not be reduced as a result of the proposed development. Social Component: This covers aspects of the wetland that provide social value and it scored well, which would be expected for a wetland interspersed within a well used recreational lake. The main categories are Economically Valuable Products, Recreational Activities, Landscape Aesthetics, Education and Public Awareness, Proximity to Areas of 9 u< ^*- Human Settlement, Ownership, and Size, and each of these have several sub-categories. It might be assumed that the Social Component score would increase as a result of use by residents of the proposed development; however the relevant categories that this might affect had already achieved maximum scores. We went through all the sub-categones line by line, and can state with confidence that the Social Component score will not be reduced as a result of the proposed development. Hydrological Component: This primarily covers flood control and water quality improvement. The main categories m the 1985 evaluation are Flow Stabilization, Water Quality Improvement, and Erosion Control. The Hydrological Component received a moderate score, with the bulk of the points coming from Flow Stabilization. We went through all the sub-categories in the Hydrological Component line by line, and can state with confidence that the Hydrological Component score will not be reduced as a result of the proposed development. Special Features Component: This component covers rarities and fish habitat, and received the highest component score. The main categories in the 1985 evaluation are Rarity and Scarcity and Significant Features & Fish and Wildlife Habitat. The bulk of the points (195) were from Rarity and Scarcity. Using the same species today, would give a score of zero in the Rarity and Scarcity component. The wetland also scored high for spawning and rearing, primarily due to the well known spawning areas further to the west. No doubt Long Bay is also important for fish spawning, but all of the houses will be more than 120 m away Scorn Long Bay. The closest the proposed road will be to potential spawnmg areas in Long Bay will be approximately 110m. Impact Statement: The proposed three houses and supporting road will not cause a decrease in the quantitative scoring of the wetland evaluation, and therefore not cause a measurable negative impact to the identified features and functions of the Loughborough Lake wetland complex. Mitigation: The western most lot contains a narrow wetland extension (about 5 to 10 m wide) of SWD3-1 (see dashed line Figure 2). This arm was not mapped as wetland in the official wetland evaluation, which would have been the correct procedure as per the wetland evaluation criteria due to its narrow width. Nevertheless, it still contains wetland that should be maintained. A lesser setback (15 m) is sufficient here as this is not officially part of the wetland and is very narrow. WOODLAND Woodland significance is not a factor in the PPS for forests in the Canadian Shield, such as Johnston Point. Loss of forest cover in general is also not an issue for Johnston Point because it is located in Westport Bcoregion 6E-10. This ecoregion contains up to 83% woodland cover and OMNR (2010) notes that woodland size is not a criterion for significance in regions with more than 60% woodland cover, and that other criteria need to be considered. 10 T"W Although woodland significance does not need to be addressed for Johnston Point, as per the PPS, we used criteria described in the OMNR (2010) we identified one feature (rarities) and two functions (water protection and erosion buffering) within the Johnston Point woodland. Feature " Rarities: We identified two Buttemut trees on the point. A BHA was undertaken and both scored "not retainable" as a result of severe canker infection. This basically means the trees are not going to survive and that there are no restrictions in regards to removing them. A formal letter of approval of the non-retainable status will be required. Since the trees are going to die, a negative impact fix>m the proposed development is not an issue. Function - Erosion Buffering: There are steep forested slopes surrounding the swamp at the eastern end of Long Bay. We recommend that no development occur within these steep sloped areas. The access road from North Shore Road en-route to Johnston Point will be avoiding the steepest slopes, but will be partly within a more gradual slope at a point that is about 60 m from the provincially significant Long Bay swamp and significant wildlife (i.e., amphibian breeding) habitat. For the purposes of erosion protection, we recommend that the road at this location (100 m of road, see *slope* in Fig. 1) have engineering and approved design standards for erosion protection. Function - Water Protection: The east basin ofLoughborough Lake is a mesotrophic warm water system, and these are not highly sensitive to development. An example of a measurable negative impact to this function might result by the removal of large areas of trees, which could result in measurable amounts of soil and debris entering the lake. In contrast, the proposed roadway within the peninsula itself will be set back more than 110 m from the edge of the lake, well beyond a zone of erosion influence. The three building footprints will be set back at least 40 m from the lake on flat land, and will have a combined footprint of less than 0.07% of Johnston Point. As a result there will be no measurable negative impact to the overall water protection function of Johnston Pomt. (Note: lesser setback distances (35m) may be possible if it can be shown that the land slopes away from the lake, such that stormwater will have a longer route than 35 m to the lake). SIGNIFICANT WILDLIFE HABFTAT The Significcsnt Wildlife Habitat Technical Guide (OMNR 2000) and Criteria Schedules (OMNR 2009) outline several categories m Ecoregion 6E that will be covered. These include habitat of seasonal concentrations of animals, rare vegetation communities, specialized habitats for wildlife, habitat of species of conservation concern, and animal .< 1 I 11 .. f ff movement corridors. All are discussed below, mcluding tine impact potential of any wildlife habitat that was determined to be significant. Significant Wildlife Habitat" Habitat of Seasonal Concentration of Animals Habitat of seasonal concentration of animals includes the following nine sub-categones: i) Waterfowl stopover and staging areas: OMNR (2009) suggests aggregations of 100 or more of listed species and 2-3 birds/ha for 7-20 days as a criteria for significance. Although water stopover occurs in Long Bay, we saw no evidence of the threshold numbers during spring field work. Regardless of this, none of the proposed buildings will be within 120 m of the bay. ii) Colonial bird nesting sites: Colonial bird nesting sites are relatively easy to discern, and threshold examples provided by OMNR (2009) include 100 Herring Gull nests or 75 Caspian Tem nests. There is no evidence of colonial bird nesting in the wetland. iii) Shorebird migratory stopover sites: Significant migratory shorebird stopover sites are typically found on large mud flats, or flat shallow water areas, and are usually known to local resource agencies or naturalist clubs. OMNR (2009) suggests the presence of 3 or more listed species and.greater than 1000 shorebird use days as criteria of significance. There is no suitable shorebird migratory stopover sites. iv) Songbird migratory stopover areas: These areas are often associated with woodlots greater than lOha. in size and withm 5 km of Lake Ontario, where migrating songbirds need to rest after crossing the expanse of open water. OMNR (2009) suggests use of a woodlot by 35 or more migratory bird species as significant. The subject property is greater than 5 km from Lake Ontario, and we found no evidence of significant songbird stopover use. v) Raptor wintering areas: OMNR (2009) suggests use of an area by two or more listed spp. and ten or more individuals. Although the site was not visited in winter, it does not have good attributes as a raptor wintering area. vi) Bat hibemacula: Bat bibemation in the region tends to be diffusely spread out in buildings and some trees, although some well known cave areas are recognized for their significance. There are no known bat hibemacula of any significance within the subject property. We also did not observe signs of any hibemacla. vii) Migratory butterfly stopovcr area: Similar to migratory songbird stopover areas, most significance butterfly stopover areas would be found within 5 km of the northern shore of Lake Ontario. OMNR (2009) suggests numbers of Monarch butterflies use days from 100-500. The subject property is greater than 5 km from Lake Ontario, and does not have unique attributes for migratory butterfly stopover. vit) Reptile hibernacula: Reptile hibemacula include both snake and turtle overwintering sites. We found no obvious snake or turtle hibemacula on Johnston 12 Point, including the four potential building sites. However snakes are ubiquitous throughout die region and it is recommended that when the specific building sites are surveyed, that a last check for hibemacula at that location be undertaken. If hibemacula are found, building relocation will have to be undertaken. viii) Winter deer yards: The significant winter deer yards (Stratum 1) in all OMNR administrative districts are usually well known. The woodlands on and adjacent to the development property have not been recognized as winter deer yards. Attributes of a winter deer yard include larger areas of heavy coniferous cover, long range movement corridors, forests free of disturbance, and adjacent active agricultural lands for foraging. We could find no evidence of heavy deer use on the subject property, nor does the property have good threshold attributes for winter deer yards. ix) Amphibian Breeding Habitat: Amphibian breeding habitat can be divided into woodland and wetland breeding habitat. For both, OMNR (2009) suggests the presence of 20 or more breeding individuals as significant. Amphibians were heard callmg m all of the swamps ofJohnston Point, but it was only in the swamp at the east end of Long Bay where calling amphibian numbers passed the threshold for significance. None of the new houses will be within 120 m of these swamps. The closest distance to the proposed road will be 60 m. The intervening distance will be forested. Impact Statement: Due to the set back distances of the road, the intervening forest, and low road use, there will be no negative impacts to amphibian breeding habitat. Significant Wildlife Habitat - Rare vegetation communities This category applies to rare ELC types, such as Alvar, Savannah, or Sand Barrens. There are no rare vegetation communities on the subject property. Significant Wildlife Habitat - Specialized habitats for wildlife Specialized habitats for wildlife are covered under the following five sub-categories. i) Waterfowl Nesting Area: OMNR (2009) suggests the presence of 3 or more nesting pairs for listed species except Mallard, or presence of 10 or more nesting pairs for listed species including Mallard. We found no evidence of this type of nesting within 120 m of any of the proposed roads or the new homes. ii) Osprey Nesting, Foraging, and Perching Habitat: Osprey use Loughborough Lake, however we did not observe any nests or active use of the subject property. iii) Woodland Raptor Nesting Habitat: We found no evidence of woodland raptor nestmg. iv) Turtle nesting habitat: We found no evidence of turtle nesting habitat. The shallow soils and dry rocky upland do not constitute good turtle nesting habitat. 13 ,;T - v) Seeps and springs: No seeps or springs were observed within the property. Significant Wildlife Habitat - Habitat for Species of Conservation Concern (not including Endangered or Threatened Species) Species of conservation concern can be those that require specialized habitat, are sensitive to human intrusion, or have some level of rarity. The six sub-categories of Species of Conservation Concern are presented below: i) Marsh Bird Breeding Habitat OMNR (2009) suggests presence of 5 or more nesting pairs ofSedge Wren or Marsh Wren or four nesting pairs for any other listed species as a threshold for significance. None were observed, and the adjacent wetlands do not constitute good marsh or sedge wren habitat. ii) Arca-Sensitive Bird Breeding Habitat: OMNR (2009) suggests mature (>60 years old) natural forest (non-plantation) stands 30 ha or greater in size and with at least 10 ha interior habitat assuming 100 m buffer at edge of forest. The forest is too young and poorly shaped to provide good area-sensitive bird breeding habitat. We found minimal evidence of use by area-sensitive species as well. iii) Open Country Bird Breeding Habitat: OMNR (2009) suggests grasslands 30 ha. or larger in size, that have two or more indicator species such as Grasshopper Sparrow or Vesper Sparrow. None of these criteria were met by the subject property. iv) Shrub Bird Breeding Habitat.OMNR (2009) suggests shrub lands 30 ha. or larger in size, that have two or more indicator species such as Brown Thrasher and Clay Coloured Sparrow. None of these criteria is met by the subject property. v) Special Concern and S1-S3 Species and Communities: This includes Sl, S2, and S3 communities, none of which were found in the development property, or within 120 m of the subject property. The Natural Heritage Information Center of Ontario lists records of rarities occurrences in the province, and for the one km. square that contains the development area the following species were listed: Cerulean Warbler (Dendroica cerulean}. SARA (Schedule I - Special Concern). The MNR record for the 2 x 1 km squares of land that encompass Johnston Point is from 1985. These birds prefer large, mature forests which are largely absent from Johnston's Point. We surveyed for these birds, which are readily identifiable by their spring call, and none were found. Five-lined Skink {Plestiodonfasciatus} SARA (Schedule 1 - Special Concern). The MNR record for fhe 2 x 1 km squares of land that encompass Johnston Point is from 1971. These animals prefer open areas of sun-exposed rock and in 1971 this 14 .n^- .^ ^ type of habitat could have been present as a result of extensive cattle grazing. Smce that time however, the canopy has filled in and rocky areas have become covered in vegetation. We could find no current evidence ofskink, or skink habitat features. Broad Beech Fern {Phegopteris hexagonopterd). SARA (Schedule 3 - Special Concern). This is a distinctive fem that is readily identifiable. The MNR record for the 2 x 1 km squares of land that encompass Johnston Point is fi-om 1980. Broad Beech Fem is found in mature older forests with rich moist soils. The bulk ofJohnsWs Point does not have Broad Beech Fern habitat. There is one small patch of about 0.3 ha of the FOM forest (see ELC Figure 3) where the habitat is appropriate, however no Broad Beech Ferns were found there. Proposed road routes number 1 and 2 pass through this area. Common Tem (Sterna hirundo}. SARA (Not at Risk). These birds were listed in the wetland evaluation (1985) as provmcially significant. Many of the species listed as provincially rare for the wetland evaluation process are no longer considered as such, and this includes the Common Tem (S4B). Regardless, they are an open water bird and would not be found in the uplands or wetlands ofJohnston Point. They are also tolerant of people, as they are commonly found within the busy Rideau waterway. Juniper Hairstreak (Callophrys gryneus). S2. These butterflies feed on juniper, which were in abundance on the Johnston Pomt peninsula in the past, but are now largely confined to a small patch near North Shore Rd. The ^access road will pass through parts of this Juniper patch. We traversed the patch in search of the Hairstreak, which are easy to observe as fhey take flight when die shrubs are shaken. However none were seen when this was done. As these Juniper patches get overgrown, as has happened with Johnston Pt, any potential butterflies will leave the area. Significant Wildlife Habitat - Animal movement corridors Animal movement corridors are needed to provide wildlife with a safe passageway between two habitats. Corridors also prevent genetic isolation, whereby an isolated population could experience higher homozygosity due to a lack ofoutbreeding. Not all species have the same corridor requirements, as animals with large home ranges will require wider longer corridors. All animals move around to some degree as part of their life cycle and any area (including urban housing) has corridor potential. As such, criteria have been set out to determine which areas arc unique (significant) and require protection. Criteria of significance can mclude wide undisturbed areas that connect significant natural areas, areas with minimal barriers, areas used by species with special requirements, and good bio-diversity. Evidence of corridor use is also useful. None of these criteria is well met 15 F^ by Johnston's Point and the fact that it dead-ends further negates its potential as significant animal movement corridor. f) Fish Habitat The fish habitat adjacent to the proposed development is warm water lacustrine and would be classified as Type II or Important habitat. This is the general term for habitat that is used for feeding and breeding by a variety of species and is common to most lakes in the area. Species known to the lake are also commonly found to most lakes in the area such as Bass, Northern Pike, Perch, Black Crappie, Pumpkinseed, and Bluegill. Sporadic nesting occurs around Johnston Point. No in-water work is proposed and it is recommended that buildings and associated buildings be set back a minimum of 40 m Irom the waters edge. Closer distances up to 35 m may be possible if it can be shown that the slopes drain away from the lake, meaning stormwater will flow over a greater distance to the lake. Septic fields will be 70 m from the water regardless. Impact Statement: In accordance of the Fisheries Act and the PPS, there will be no development within fish habitat. Construction Mitigation: As is normal for any work near fish habitat, silt screens and hay bale silt barriers should be placed between construction areas within 40 m of the lake or wetland. They should also be periodically checked to ensure proper functioning. There should be no construction activities within 30 m of fish habitat. LITERATURE CITED Henson, B.L. and K.E. Brodribb 2005. Great Lakes Conservation Blueprint for Terrestrial Biodiversity, Volume 2: Ecodistrict Summaries. Nature Conservancy of Canada. Lee, H.l., W.D. Bakowsky, J. Riley, J. Bowles, M. Puddister, P. Uhlig, and S. McMurray. 1998. Ecological land classification for Soufhem Ontario. First approximation and its application. Ontario Ministry of Natural Resources. Southcentral Science Section, Science Development and Transfer Branch. SCSS Field Guide FG -02. Ontario Ministry of Natural Resources. 2000. Significant wildlife habitat technical guide. Toronto: Queen's Printer for Ontario. 151p. Ontario Ministry of Natural Resources. 2009. Significant wildlife habitat ecoregion criteria schedules. Addendum to Significant Wildlife Habitat Technical Guide. Ontario Ministry of Natural Resources. Working Draft. 16 f^- . ini<". Ontario Ministry of Natural Resources. 2010. Natural Heritage Reference Manual for Natural Heritage Policies offae Provincial Policy Statement, 2005. Second Edition. Toronto: Queen's Printer for Ontario. 248 pp. 17 I'll ** 1<»1-U t