FINAL BASIC ASSESSMENT REPORT - Cape EAPrac Sonskynvallei...Cape EAPrac Final Basic Assessment...
Transcript of FINAL BASIC ASSESSMENT REPORT - Cape EAPrac Sonskynvallei...Cape EAPrac Final Basic Assessment...
Cape Environmental Assessment Practitioners (Pty) Ltd Reg. No. 2008/004627/07
Telephone: (044) 874 0365 1st Floor Eagles View Building
Facsimile: (044) 874 0432 5 Progress Street, George
Web: www.cape-eaprac.co.za PO Box 2070, George 6530
D.J. Jeffery Directors L. van Zyl
FINAL BASIC ASSESSMENT REPORT
For
SONSKYNVALLEI HOUSING EXTENSION – PHASE 3
On
Portions 4, 59 & 105 of the Farm Hartenbosch 217, Erf 1853 & Erf 3122, Mossel Bay
In terms of the
National Environmental Management Act (Act No. 107 of 1998, as amended) & 2010 Environmental Impact Regulations
Prepared for Applicant: Mossel Bay Municipality By: Cape EAPrac
Report Reference: MOS286/13 Department Reference: 16/3/1/1/D6/18/0070/13
Case Officer: Marianne Lesch Date: 13 November 2014
APPOINTED ENVIRONMENTAL ASSESSMENT PRACTITIONER: Cape EAPrac Environmental Assessment Practitioners
PO Box 2070 George
6530 Tel: 044-874 0365 Fax: 044-874 0432
Report written & compiled by: Wynand Loftus (MTech Nature Conservation).
Report reviewed by: Louise-Mari van Zyl (MA Geography & Environmental Science [US];
Registered Environmental Assessment Practitioner with the Interim Certification Board for
Environmental Assessment Practitioners of South Africa, EAPSA); Ms van Zyl has over twelve
years‟ experience as an environmental practitioner.
PURPOSE OF THIS REPORT: Environmental Authorisation
APPLICANT: Mossel Bay Municipality
CAPE EAPRAC REFERENCE NO: MOS286/13
DEPARTMENT REFERENCE: 16/3/1/1/D6/18/0070/13
SUBMISSION DATE 13 November 2014
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FINAL BASIC ASSESSMENT REPORT
in terms of the National Environmental Management Act, 1998 (Act No. 107 of 1998), as amended & Environmental
Impact Regulations 2010
Sonskynvallei Housing Extension – Phase 3 Portions 4, 59 & 105 of the Farm Hartenbosch 217, Erf 1853 & Erf 3122, Mossel Bay
Submitted for: Stakeholder Review & Comment This report is the property of the Author/Company, who may publish it, in whole, provided that: Written approval is obtained from the Author and that Cape EAPrac is acknowledged in the
publication; Cape EAPrac is indemnified against any claim for damages that may result from any publication of
specifications, recommendations or statements that is not administered or controlled by Cape EAPrac;
The contents of this report, including specialist/consultant reports, may not be used for purposes of sale or publicity or advertisement without the prior written approval of Cape EAPrac;
Cape EAPrac accepts no responsibility by the Applicant/Client for failure to follow or comply with the recommended programme, specifications or recommendations contained in this report;
Cape EAPrac accepts no responsibility for deviation or non-compliance of any specifications or recommendations made by specialists or consultants whose input/reports are used to inform this report; and
All figures, plates and diagrams are copyrighted and may not be reproduced by any means, in any form, in part or whole without prior written approved from Cape EAPrac.
Report Issued by: Cape Environmental Assessment Practitioners
Tel: 044 874 0365 PO Box 2070 Fax: 044 874 0432 5 Progress Street Web: www.cape-eaprac.co.za George 6530
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ORDER OF REPORT Executive Summary
Basic Assessment Report
Appendix A : Location & Topographical Map
Appendix B : Site Layout Plans
Appendix C : Site Photos
Appendix D : Biodiversity Overlays
Annexure D1 : Critical Biodiversity Area (CBA) Map
Annexure D2 : Vegetation Map
Annexure D3 : National Freshwater Ecosystem Priority Area (NFEPA) Map
Appendix E : Permits and Approvals
Annexure E1 : ATKV Letter of Consent to Develop
Annexure E2 : Availability of Electrical Services
Annexure E3 : Availability of Water & Waste Capacity
Appendix F : Public Participation Information
Annexure F1 : Initial Notification, Advert, Site Notice & Correction Notice
Annexure F2 : Registrations Received
Annexure F3 : Meeting Minutes and Attendance Registers
Annexure F4 : Initial Issues and Comments
Annexure F5 : Draft BAR Notifications
Annexure F6 : Comments Received on Draft BAR
Annexure F7 : Final BAR Notifications
Annexure F8 : Comments and Response Table
Annexure F9 : Stakeholder Register (registered I&APs)
Appendix G : Specialist Reports
Annexure G1 Archaeological Impact Statement
Annexure G2 : Botanical Impact Assessment
Annexure G3 : Civil Services Report
Annexure G4 : Electrical Services Report
Annexure G5 : Heritage Assessment
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Annexure G6 : Planning Statement
Annexure G7 : Traffic Impact Assessment
Annexure G8 : Visual Impact Statement
Appendix H : Construction Phase Environmental Management Programme
Appendix I : Background Information Document (BID)
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TABLE OF CONTENTS
BASIC ASSESSMENT FORM .................................................................... 1
SUMMARY ................................................................................................. 4
1. INTRODUCTION ................................................................................................................................... 4 1.1 PROJECT NEED................................................................................................................................ 4
2. PROCESS DESCRIPTION ................................................................................................................... 4 3. ACTIVITY & PLANNING CONTEXT .................................................................................................... 5 4. SITE DESCRIPTION AND ATTRIBUTES ............................................................................................ 7 5. PROCESS TO DATE ............................................................................................................................ 8 6. IMPACT SUMMARY ............................................................................................................................. 9 7. CONCLUSION .................................................................................................................................... 10
SECTION A: ACTIVITY INFORMATION .................................................. 12
1 PROJECT DESCRIPTION .................................................................................................................. 12 1.1 INFRASTRUCTURE DESCRIPTION ..................................................................................................... 23
2. PHYSICAL SIZE OF THE ACTIVITY.................................................................................................. 33 3. SITE ACCESS ..................................................................................................................................... 33
4. DESCRIPTION OF THE PROPERTY ON WHICH THE ACTIVITY IS TO BE UNDERTAKEN AND THE LOCATION OF THE ACTIVITY ON THE PROPERTY ............................................................. 34 5. SITE PHOTOGRAPHS ....................................................................................................................... 43
SECTION B: DESCRIPTION OF RECEIVING ENVIRONMENT ............... 44
1. SITE/AREA DESCRIPTION ................................................................................................................ 44 2. GRADIENT OF THE SITE .................................................................................................................. 44 3. LOCATION IN LANDSCAPE .............................................................................................................. 44 4. GROUNDWATER, SOIL AND GEOLOGICAL STABILITY OF THE SITE ........................................ 46 5. SURFACE WATER ............................................................................................................................. 47 6. BIODIVERSITY ................................................................................................................................... 47 7. LAND USE OF THE SITE ................................................................................................................... 50 8. LAND USE CHARACTER OF SURROUNDING AREA ..................................................................... 50 9. SOCIO-ECONOMIC ASPECTS .......................................................................................................... 51 10. HISTORICAL AND CULTURAL ASPECTS ....................................................................................... 53 11. APPLICABLE LEGISLATION, POLICIES AND/OR GUIDELINES ................................................... 55
SECTION C: PUBLIC PARTICIPATION ................................................... 58
SECTION D: NEED AND DESIRABILITY ................................................ 64
SECTION E: ALTERNATIVES ................................................................. 70
SECTION F: IMPACT ASSESSMENT, MANAGEMENT, ......................... 73
MITIGATION AND MONITORING MEASURES ....................................... 73
1. DESCRIBE THE MANNER IN WHICH THE DEVELOPMENT WILL IMPACT ON THE FOLLOWING ASPECTS: ........................................................................................................................... 73 2. WASTE AND EMISSIONS .................................................................................................................. 77
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3. WATER USE ....................................................................................................................................... 78 4. POWER SUPPLY ................................................................................................................................ 79
4.1 ENERGY EFFICIENCY ............................................................................................................... 79
5. DESCRIPTION AND ASSESSMENT OF THE SIGNIFICANCE OF IMPACTS PRIOR TO AND AFTER MITIGATION .................................................................................................................................. 80 6. SPECIALIST INPUTS/STUDIES AND RECOMMENDATIONS ....................................................... 104 7. IMPACT SUMMARY ......................................................................................................................... 108 8. OTHER MANAGEMENT, MITIGATION AND MONITORING MEASURES .................................... 109
SECTION G: ASSESSMENT METHODOLOGIES AND CRITERIA, GAPS IN KNOWLEDGE, UNDERLAYING ASSUMPTIONS AND UNCERTAINTIES ................................................................................... 111
SECTION H: RECOMMENDATION OF THE EAP ................................. 113
SECTION I: APPENDICES ..................................................................... 115
DECLARATIONS.................................................................................... 116
1. THE APPLICANT .............................................................................................................................. 116 2. THE INDEPENDENT ENVIRONMENTAL ASSESSMENT PRACTITIONER (EAP) ....................... 117 3. THE INDEPENDENT PERSON WHO COMPILED A SPECIALIST REPORT OR UNDERTOOK
A SPECIALIST PROCESS ....................................................................................................................... 118
REFERENCES ....................................................................................... 119
LIST OF FIGURES Figure 1: Google Earth image showing the alignment of the proposed new bulk water pipeline to
service the proposed development – imagery date September 2013 (Google Earth, 2014). The existing road leading up to the Hartenboskop reservoir from Sonskynvallei is also visible on the image. .......................................................................................................................................... 13
Figure 2: Route of the proposed new bulk water line from the Hartenboskop reservoir to the site. The figure also illustrates the route of the proposed new sewer rising main for the proposed development (Du Preez, 2014). .................................................................................................. 14
Figure 3: The proposed alignment of the new pipeline is indicated in the figure. The Botanical specialist recommends that where the servitude ends, the pipeline follows the alignment of the existing road leading up to the Hartenboskop reservoir and not as indicated by the blue line. .. 15
Figure 4: The pipeline alignment as recommended by the specialists is illustrated. It is recommended that the pipeline follow the alignment of an existing track leading to the Hartenboskop reservoir. ..................................................................................................................................................... 16
Figure 5: Map illustrating the location and short description of infrastructure upgrades proposed for Phase 3 of Sonskynvallei Housing. The map does not include the proposed new water pipeline and reservoir upgrade as these are described earlier in this report. .......................................... 23
Figure 6: Vegetation along the southern section of the R328 where the walkway is proposed, note that the vegetation directly adjacent to the road consist of grasses. At this particular point a milkwood (indicated by arrow) is within close proximity of the road. It is anticipated that if construction occurs within demarcated areas, this milkwood will not be affected. In the
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background, where the white bakkie is, is the Mandela Street turnoff to Sonskynvallei. The Department Transport and Public Works have recommended that the turnoff in the foreground be closed. This photo was taken looking in a north easterly direction along the R328. ............. 24
Figure 7: This photo was taken from same position as Figure 6 looking in a south easterly direction towards Hartenbos along the R328. Vegetation directly adjacent to the road consists of grasses and there are no protected trees found along this stretch up to Waboom Street (where walkway is proposed to stop). Reeds seen in this photo is associated with stormwater runoff from the road ............................................................................................................................................. 25
Figure 8: The photo was taken looking back towards Sonskynvallei at the approximate halfway mark between Mandela and Waboom Street. Vegetation is sparse and consists of grasses. ............ 25
Figure 9: This photo was taken at the same location as Figure 7, looking in the opposite direction, towards Hartenbos. The turnoff to Waboom Street can be seen in the background. Impact on vegetation along this section is also considered to be negligible. .............................................. 25
Figure 10: The access point referred to as „waste disposal‟ in comment received from the Department of Transport and Public Works which the Department to be closed off. The waste disposal site can be seen in the background, behind the white wall ............................................................... 26
Figure 11: The waste disposal site at Sonskynvallei, which will be accessed via Mandela Street in future. .......................................................................................................................................... 26
Figure 12: This photo was taken from the „waste disposal‟ access point (to be closed off) looking towards the Mandela Street access point (seen in the background where the bakkie is) situated approximately 50m from where this photo was taken. There will therefore be ample space to construct a left turning lane with minimum length of 30m. From the figure it is clear that the impact on vegetation is negligible. .............................................................................................. 27
Figure 13: The Gumpiro Avenue access point. It was recommended by the TIA and Dept. Transport and Public Works that this access point be closed. This photo was taken in a westerly direction, showing the R328 to Oudtshoorn on the right and the clinic and community centre on the left in the background. ........................................................................................................................... 28
Figure 14: The two photos were taken from the existing Gumpiro Avenue access point (to be closed). The photo on the left is taken in the direction of Oudtshoorn and the photo on the right in the direction of Hartenbos. ................................................................................................................ 28
Figure 15: The height difference between the road and site is illustrated in this picture. In the foreground is an access point for a PetroSA water line indicated in the site development plan. No development will take place on the water line servitude ....................................................... 29
Figure 16: It is proposed that the new pump station be constructed on the grassed area on the left of this photo. This area was assessed by the botanical specialist and found suitable for development. Areas seen on the right hand side of this photo has been excluded from the development area as it has been identified as sensitive and conservation worthy by the specialist ...................................................................................................................................... 29
Figure 17: The new rising main will start at the existing Sonskynvallei pump station and travel in a north westerly direction (photo on the right) toward the location of the new pump station. ........ 30
Figure 18: The vegetation along Gumpiro Avenue road reserve where rising main is proposed to be installed. The Sonskynvallei pump station is visible in the background ...................................... 30
Figure 19: The vegetation along Gumpiro Avenue is illustrated looking in a north westerly direction towards the current Gumpiro Avenue access point. The rising main is proposed to be installed on the left of the fence seen in this photo ................................................................................... 31
Figure 20: Vegetation along the rising main route in the northern corner of the proposed development site/north of the clinic. This vegetation was assessed as part of the botanical specialist assessment and not found to be sensitive .................................................................................. 31
Figure 21: The photo shows, from the left, the R328, stormwater channel next to the road and the Gumpiro Avenue road reserve. Sonskynvallei pump station is visible in the background, along the road reserve. It would be impractical to align the sewer rising main in the stormwater channel next to the road, therefore the Gumpiro Avenue road reserve is recommended to be more suitable. .............................................................................................................................. 32
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Figure 22: Area of the proposed site that has been identified for housing development (location of the housing activity on the property) i.e. outlined in yellow is the proposed area where the houses will physically be built, Public Open Space is excluded. ............................................................. 35
Figure 23: Proposed alignment of the new bulk water pipeline. ............................................................ 36
Figure 24: Proposed new pipeline alignment as recommended by specialists. The proposed new alignment means a section of the pipeline will be aligned an along an existing track leading to the Hartenboskop reservoir. ........................................................................................................ 37
Figure 25: The existing Hartenboskop reservoir is seen in the background. Vegetation around the site comprises a mixture of indigenous and alien plants. The botanical specialist described the vegetation close (and around) the reservoir as „somewhat transformed‟. The fence around the reservoir site has been largely destroyed and vandalised. The photo was taken in a westerly direction. ...................................................................................................................................... 38
Figure 26: Vegetation at the Hartenboskop reservoir. Photo taken from the reservoir to the where Figure 25 was taken from, in a north-easterly direction. ............................................................. 38
Figure 27: Alignment of proposed bulk water pipeline to service the proposed development. The pipeline will start at the existing Hartenboskop reservoir and be approximately 1.4km in length – imagery date September 2013 (Google Earth, 2014). ................................................................ 40
Figure 28: Slope (in degrees) of the proposed development area is indicated in the figure. Map was generated on CapeFarmMapper – Western Cape Department of Agriculture (CapeFarmMapper, 2014) ........................................................................................................................................... 44
Figure 29: Location of the development site in the landscape indicating the R328 between Hartenbos and Oudtshoorn (Google Earth, 2014). ....................................................................................... 45
Figure 30: Contour plan (5m) of the proposed Sonskynvallei development site. The figure illustrates the proposed new bulk water pipeline alignment as recommended by specialists (line) and the proposed development site (polygon). Please note that the area identified for housing development does not comprise the entire development site as indicated in this figure, refer to Appendix B – Development layout. Map was generated on CapeFarmMapper – Department of Agriculture (CapeFarmMapper, 2014) ........................................................................................ 45
Figure 31: The figure above is from Coetzee (2014), and illustrates areas of the proposed development site (yellow) in terms of their sensitivity. Areas 1 -3 indicate thicket vegetation and 4 indicate an area that has been mostly transformed. ................................................................ 49
Figure 32: The figure illustrates the land uses surrounding the development site. ............................... 51
Figure 33: 3D images of the proposed structures for the Sonskynvallei Phase 3 housing extension. Single free-standing units are illustrated in the back and semi-detached in the front (Stead, 2014). .......................................................................................................................................... 71
Figure 34: Urban Edge of Mossel Bay indicated by the blue dotted line. From the image it is clear that the existing Sonskynvallei Township as well as the proposed new development area (except for a portion of the new bulk water pipeline) falls within the urban edge of Mossel Bay (Mossel Bay SDF, 2008). ............................................................................................................................... 108
LIST OF TABLES Table 1: Coordinates of the proposed water pipeline from the existing Hartenboskop reservoir to the
proposed Phase of the Sonskynvallei housing development...................................................... 41
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ABBREVIATIONS AIA Archaeological Impact Assessment BGIS Biodiversity Geographic Information System BID Background Information Document CBD Central Business District ACMP Archaeological Conservation Management Plan CDSM Chief Directorate Surveys and Mapping CEMP Construction Environmental Management Plan DBAR Draft Basic Assessment Report DEA Department of Environmental Affairs DEA&DP Department of Environmental Affairs and Development Planning DME Department of Minerals and Energy FBAR Final Basic Assessment Report EAP Environmental Impact Practitioner EHS Environmental, Health & Safety EIA Environmental Impact Assessment EIR Environmental Impact Report EMP Environmental Management Programme GPS Global Positioning System HIA Heritage Impact Assessment HWC Heritage Western Cape I&APs Interested and Affected Parties IDP Integrated Development Plan LLRC Low Level River Crossing LUDS Land Use Decision Support LUPO Land Use Planning Ordinance MW Mega Watt NEMA National Environmental Management Act NEMAA National Environmental Management Amendment Act NEMBA National Environmental Management: Biodiversity Act NERSA National Energy Regulator of South Africa NHRA National Heritage Resources Act NID Notice of Intent to Develop NSBA National Spatial Biodiversity Assessment NWA National Water Act PM Post Meridiem; “Afternoon” SACAA South African Civil Aviation Authority SAHRA South African National Heritage Resources Agency SANBI South Africa National Biodiversity Institute SANS South Africa National Standards SDF Spatial Development Framework SAPD South Africa Police Department TIA Traffic Impact Assessment VIA Visual Impact Assessment
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BASIC ASSESSMENT REPORT (AUGUST 2010)
BASIC ASSESSMENT FORM
(AUGUST 2011) Basic Assessment Report in terms of the NEMA Environmental Impact Assessment
Regulations, 2010 AUGUST 2010
Kindly note that: 1. This Basic Assessment Report is the standard report required by DEA&DP in terms of the EIA Regulations, 2010 and
must be completed for all Basic Assessment applications. 2. This report must be used in all instances for Basic Assessment applications for an environmental authorisation in terms of
the National Environmental Management Act, 1998 (Act No. 107 of 1998) (NEMA), as amended, and the Environmental Impact Assessment Regulations, 2010, and/or a waste management licence in terms of the National Environmental Management: Waste Act, 2008 (Act 59 of 2008) (NEM: WA), and/or an atmospheric emission licence in terms of the National Environmental Management: Air Quality Act, 2004 (Act No. 39 of 2004) (NEM: AQA).
3. This report is current as of 2 August 2010. It is the responsibility of the Applicant / EAP to ascertain whether subsequent
versions of the report have been published or produced by the competent authority.
4. The required information must be typed within the spaces provided in the report. The sizes of the spaces provided are not necessarily indicative of the amount of information to be provided. It is in the form of a table that will expand as each space is filled with typing.
5. Incomplete reports will be rejected. A rejected report may be amended and resubmitted. 6. The use of “not applicable” in the report must be done with circumspection. Where it is used in respect of material
information that is required by the Department for assessing the application, this may result in the rejection of the report as provided for in the regulations.
7. While the different sections of the report only provide space for provision of information related to one alternative,
if more than one feasible and reasonable alternative is considered, the relevant section must be copied and completed for each alternative.
8. Unless protected by law all information contained in, and attached to this report, will become public information on receipt
by the competent authority. If information is not submitted with this report due to such information being protected by law, the applicant and/or EAP must declare such non-disclosure and provide the reasons for the belief that the information is protected.
9. This report must be submitted to the Department at the postal address given below or by delivery thereof to the Registry
Office of the Department. No faxed or e-mailed reports will be accepted. Please note that for waste management licence applications, this report must be submitted for the attention of the Department’s Waste Management Directorate (tel: 021-483-2756 and fax: 021-483-4425) at the same postal address as the Cape Town Office Region A.
10. Unless indicated otherwise, two electronic copies (CD/DVD) and three hard copies of this report must be submitted to the
Department.
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DEPARTMENTAL DETAILS CAPE TOWN OFFICE REGION A (Cape Winelands, City of Cape Town: Tygerberg and Oostenberg Administrations)
CAPE TOWN OFFICE REGION B (West Coast, Overberg, City of Cape Town: Helderberg, South Peninsula, Cape Town and Blaauwberg Administrations
GEORGE OFFICE (Eden and Central Karoo)
Department of Environmental Affairs and Development Planning Attention: Directorate: Integrated Environmental Management (Region A2) Private Bag X 9086 Cape Town, 8000 Registry Office 1st Floor Utilitas Building 1 Dorp Street, Cape Town Queries should be directed to the Directorate: Integrated Environmental Management (Region A2) at: Tel: (021) 483-4793 Fax: (021) 483-3633
Department of Environmental Affairs and Development Planning Attention: Directorate: Integrated Environmental Management (Region B) Private Bag X 9086 Cape Town, 8000 Registry Office 1st Floor Utilitas Building 1 Dorp Street, Cape Town Queries should be directed to the Directorate: Integrated Environmental Management (Region B) at: Tel: (021) 483-4094 Fax: (021) 483-4372
Department of Environmental Affairs and Development Planning Attention: Directorate: Integrated Environmental Management (Region A1) Private Bag X 6509 George, 6530 Registry Office 4th Floor, York Park Building 93 York Street George Queries should be directed to the Directorate: Integrated Environmental Management (Region A1) at: Tel: (044) 805 8600 Fax: (044) 874-2423
View the Department’s website at http://www.capegateway.gov.za/eadp for the latest version of this document.
DEPARTMENTAL REFERENCE NUMBER(S) File reference number (EIA): File reference number (Waste): File reference number (Other): PROJECT TITLE Sonskynvallei Housing Extension – Phase 3
DETAILS OF THE ENVIRONMENTAL ASSESSMENT PRACTITIONER (EAP) Environmental Assessment Practitioner (EAP):
Cape Environmental Assessment Practitioners (Pty) Ltd
Contact person: Wynand Loftus Postal address: P O Box 2070 George Postal code: 6530 Telephone: (044) 874 0365 Cell: 072 354 2607 E-mail: [email protected] Fax: (044) 874 0432 EAP Qualifications MTech Nature Conservation (Nelson Mandela Metropolitan University)
EAP Registrations/Associations
Director certified as an Environmental Assessment Practitioners with the
Interim Certification Board for Environmental Assessment Practitioners of
South Africa (EAPSA).
DETAILS OF THE EAP‟S EXPERTISE TO CARRY OUT BASIC ASSESSMENT PROCEDURES Wynand Loftus (MTech Nature Conservation, NMMU) has a Master‟s degree, completed in 2013,
focused on the Invasive Alien Plants management and the effectiveness thereof in South African
National Parks. The main conceptual foundation of his Master‟s was Strategic Adaptive Management,
specifically focussing on whether this management paradigm is being implemented (practically) on the
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ground.
As part of his BTech Nature Conservation, Wynand completed a subject that focuses on the National
Environmental Management Act (NEMA) and the environmental process that needs to take place as
described in the act (e.g. this report). Amongst others, he also has experience in resource
management (erosion & fire management), plant identification & statistics, which formed part of his
study career.
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EXECUTIVE SUMMARY OF THE CONTENT OF THE BASIC ASSESSMENT REPORT:
SUMMARY
1. INTRODUCTION
Cape Environmental Assessment Practitioners (Cape EAPrac) has been appointed by the Mossel
Bay Municipality as independent environmental assessment practitioners (EAP) to investigate and
assess the environmental impact of a proposed housing development on Portions 4, 59 & 105 of the
Farm Hartenbosch 217, Erf 1853 and Erf 3122, Mossel Bay.
The development triggers a number of “listed activities” in terms of the 2010 Environmental
Regulations and National Environmental Management Act (Act 107 of 1998 as amended) for which
prior authorisation must be obtained from the Provincial Department of Environmental Affairs.
In order to investigate and assess the potential impacts associated with the proposed development a
Basic Assessment process must be undertaken. Such a process is to be informed by specialist and
project team input. This report includes reference to such studies and uses the information gathered
by specialists to determine the nature and significance of impacts that may result from the proposed
development.
Please note that for ease of reference, any information that did not appear in the Draft BAR is
highlighted in dark grey in this Final BAR.
1.1 PROJECT NEED The Mossel Bay Municipality, as the local authority, has a mandate and responsibility to provide in the
housing need of those that cannot secure/afford accommodation. As part of this mandate the
Municipality maintains a housing list of beneficiaries that qualify for assistance / subsidies and based
on the demand the Municipality investigate and implements housing projects to address the housing
backlog.
The Municipality has identified the proposed site as suitable for one of their housing projects within the
greater Mossel Bay area. There is a constant influx of people into the Sonskynvallei community and
housing shortages need to be addressed. The property falls within the urban edge of Mossel Bay
and has been earmarked for future township expansion.
2. PROCESS DESCRIPTION
This Final Basic Assessment Report (FBAR) is the third, and final, in a series of three (3) reports
that make up the Basic Assessment process. The first being the Application Form that was submitted
to the Department of Environmental Affairs and Development Planning (DEA&DP) on 19 November
2013 and accepted by them on 5 December 2013. The second being the Draft Basic Assessment
Report (DBAR) which was made available to the public, and authorities, for a 40-day commenting
period (1 October 2014 to 10 November 2014).
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Public participation commenced with written notice to neighbouring land owners, newspaper adverts
and site notices, calling for the registration of Interested & Affected Parties (I&APs) to register for the
process and/or submit preliminary comments if relevant.
The above steps were followed by a meeting with the local Councillor, relevant Municipal departments,
planner and Cape EAPrac to obtain input and guidance on aspects that must be taken into account
during the environmental process. The public participation process was informed by a meeting
between the ward committee and the persons mentioned above.
This FBAR (3rd of the three reports) will be available for a period of 21-days during which time
registered I&APS, Key Stakeholders, relevant Authorities and Organs of State will be allowed time to
review the report and formulate their comments. Once the comment period ends on the FBAR, Cape
EAPrac will consult with the relevant project team members and specialists to reflect on any
changes/amendments that may be required in order to address and/or mitigate further
issues/concerns not yet identified. All comments received during the specified comment period will be
considered, responded to, and recorded in the Final Basic Assessment Report (FBAR) which will be
submitted to the Department of Environmental Affairs and Development Planning (DEA&DP). The
FBAR is the final report of the environmental process. Any changes to the proposal and submissions
are included in this FBAR.
Once the comment period on the FBAR ends, the report will be submitted to the delegated decision-
making Authority (DEA&DP, George) for consideration and decision-making.
All registered I&APs will be informed of the Department’s decision on the application.
3. ACTIVITY & PLANNING CONTEXT
Two development alternatives have been considered in the planning phase of this process. Alternative
3 (Status Qua/No-Go) is not considered feasible as it does not present the most optimal use for the
site since the property falls within the urban edge and has been earmarked for township expansion.
The impacts of Alternative 3 are however assessed against other alternatives. The following
alternatives are considered in this application (values appearing below are approximate):
Alternative 1
Appendix B, layout map dated January 2014
- 686 Residential Zone (subsidy) erven (free-
standing single dwellings)
- 2 Transport Zone II erven
- 14 Public Open Space erven
- 2 Church erven
- 1 Crèche erf
- 1 Business erf
- 1 Authority erf
Limited specialist input ito of sensitive natural areas
that must be avoided and visual impact.
Alternative 2 (preferred) - 616 Residential Zone (subsidy) erven (semi-
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Appendix B, layout map
dated November 2014
detached dwellings)
- 2 Transport Zone II erven
- 11 Public Open Space erven
- 2 Church erven
- 1 Crèche erf
- 1 Business erf
- 1 Authority erf
Layout informed through specialist input. Areas with
sensitive vegetation have been excluded from
development footprint. Visual impact statement
identified that a number of erven be removed to
decrease visual impact – reflected in this plan. The
Department of Transport & Public Works
recommended that the layout be amended to
accommodate a possible future access point opposite
the mine – recommendation take into account in this
layout.
Alternative 3 No development takes
place Status Quo/No-Go
The properties are currently zoned Agriculture and Authority respectively, thus re-zoning of the site is
required to allow for the erven in the table above.
The Municipality has confirmed that services (electricity and household waste) can be supplied to the
development (Annexure E2 & E3). Infrastructure upgrades are however required for the water
provisioning and sewage, as indicated in the civil services report. The report compiled by Du Preez
(2014) indicated that the following upgrades be made in order to service the proposed development:
- 1200kl capacity increase to the existing Hartenboskop reservoir (new reservoir)
- New 200mm bulk water pipeline from the Hartenboskop reservoir to the proposed
development
- New sewer rising main with pump station (within the development footprint)
Where relevant the environmental impact of the new bulk services were considered and assessed in
this document.
The proposed development will have an approximate footprint of 33.76ha, of which ± 14.6ha will be
developed as housing opportunities with associated infrastructure, and ±19.1ha will be zoned Public
Open Space.
It has to be noted that although the proposed development makes provision for a high number of
housing opportunities, not all housing opportunities will be developed simultaneously. Prior to
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Cape EAPrac 7 Final Basic Assessment Report
Phase 3 (of Sonskynvallei) being implemented, Phase 2 (approved and serviced) must be occupied
first, only later to be followed by Phase 3 (this application). It is anticipated that this application (for
Phase 3 of Sonskynvallei) will be implemented over a 5 – 10 year period.
The proposed development site will be serviced and housing opportunities will be developed as per
the need and availability of municipal funds.
4. SITE DESCRIPTION AND ATTRIBUTES
Farm Portions 59 & 105 of the Farm Hartenbosch 217 and Erf 1853 are owned by the Mossel Bay
Municipality (the Applicant). Erf 3122 and Portion 4 of the Farm Hartenbosch 217 are owned by the
ATKV (Afrikaanse Taal- en Kultuurvereniging) who have granted the Applicant permission to conduct
an environmental impact assessment and develop the property for the goal of subsidy housing
opportunities (Annexure E1).
PROPERTY ZONING SIZE COORDINATES 21 SG DIGIT
Farm Portion 59 of 217 Agricultural Zone I 16.7
34˚07‟10.36”S
22˚05‟03.21”E C05100000000021700059
Farm Portion 105
of 217 Institutional Zone I 6.5ha 34˚06‟53.67”S
22˚04‟57.44”E C05100000000021700105
Erf 1853 Agricultural Zone I 151.8ha
34˚07‟18.77”S
22˚05‟25.06”E C05100040000185300000
Erf 3122 Agricultural Zone I 60.5ha
34˚07‟39.11”S
22˚05‟04.55”E C05100040000312200000
Remainder of
Farm Portion 4 of
217 Agricultural Zone I 43.2
34˚07‟11.25”S
22˚04‟48.54”E C05100000000021700004
The development site can be described as an undeveloped area located between a housing suburb to
the east (existing Sonskynvallei Township), brickworks to the west, agricultural land to the north and a
„natural‟ area to the south. Five (5) properties make up the development site. In total these properties
covers an area of ±278ha. The proposed development will however be restricted to an approximate
footprint of 33.76ha. The site is located approximately 2km west of the N2 between Hartenbos and
Klein Brak, along the R328 that travels between Hartenbos and Oudtshoorn. Access to the site would
be via the existing R328 and Mandela Street as recommended and indicated in the Traffic Impact
Assessment (TIA; Annexure G6).
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Cape EAPrac 8 Final Basic Assessment Report
According to SANBI BGIS the entire site is described as Groot Brak Dune Strandveld and classified
as ‘Endangered’ in terms of ecosystem status, and ‘not protected’ in terms of protection status. This
vegetation type is associated with flat undulating landscapes and steep coastal slopes. At a finer scale
the vegetation has been described as Herbertsdale Renoster Thicket which is characterised by
small thicket clumps occurring in a matrix of Renosterveld. The Renosterveld component of the
vegetation is very grassy in the areas most recently burnt. True thicket occurs west of the rugby field
(Coetzee, 2014).
In overall context the land use of the site can be described as natural/undeveloped. There is also a
rugby field, netball court (under construction), crèche and clinic on the site. These facilities are
currently used by people from the existing Sonskynvallei Township (Phase 1). The proposed
development, Phase 3, will in-part be constructed around the rugby field, crèche and clinic. Most of the
development will be constructed on an area described as natural.
5. PROCESS TO DATE
CHRONOLOGY OF EVENTS DATE PURPOSE ENTITY ACTIONS 19 November 2013 Application form for
Basic Assessment DEA&DP Submitted
5 December 2013 Application accepted DEA&DP Environmental Process to commence
13 June 2014 Public Participation Process (PPP): Advert calling I&APs to register
George Herald Calling I&APs to register for the Environmental Process
13 June 2014 PPP: Placing of two (2) site notices
Proposed development site
Informing of the project proposal, deviations and exemption, as well as how to register as an I&AP
13 June 2014 PPP: notification of Environmental Process
Neighbouring landowners, ward councillor, relevant state departments and authorities
Informing of the Environmental Process and how to register as an I&AP if not already registered. Also ask to submit any provisional comments. Direct neighbours of Sonskynvallei were informed via letter drop.
20 June 2014 Meeting with ward Councillor, planners, Mossel Bay Municipality Housing & Environmental Managers
Mossel Bay Municipality
Discuss future ward committee meeting, visual impact statement will be required, BID will need to be compiled (in Afrikaans), explore possibility of semi-detached dwellings.
23 June 2014 Compose Afrikaans Background Information Document
Cape EAPrac BID was prepared to provide more information to
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Cape EAPrac 9 Final Basic Assessment Report
(BID) community members and relevant authorities.
2 July 2014 Ward committee meeting
Sonskynvallei and Hartenbosheuwels Ward Committees and Mossel Bay Municipality
Discuss the project and hand out BID‟s to attendees.
14 July 2014 Distribute BID to registered I&APs, relevant state departments and authorities
Various Provide information of proposed development.
29 September 2014 Submit DBAR DEA&DP DBAR made available for 40-day commenting period.
1 October 2014 Start of 40-day commenting period on DBAR. DBAR hard copy made available at the Mossel Bay Municipality‟s Planning Department, Hartenbos Library and Sonskynvallei Clinic. Digital Copy available on the Cape EAPrac website.
Document made available by Cape EAPrac.
Start of 40-day commenting period on DBAR.
10 November 2014 End of 40-day commenting period on DBAR
11 November 2014 Send out Notifications of the Availability of the FBAR from 13 November to 3 December 2014. FBAR will be submitted at the same time as start of commenting period
Registered I&APs. Notification of start of 21-day commenting period.
12 November 2014 Submit Final BAR DEA&DP Final BAR made available for 21-day commenting period at same date as submission.
6. IMPACT SUMMARY
The change in character of the area from an undeveloped portion of land to an urban township
is low negative considering that the property falls within the urban edge of Mossel Bay, which
renders the change acceptable as it is designated for township development.
The loss of biodiversity associated with the clearing of vegetation and the transformation of
portions of the site for housing development is considered low/medium negative. The reason
for this impact rating is due to the land currently being undeveloped and containing remnants
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Cape EAPrac 10 Final Basic Assessment Report
of natural vegetation. Conservation worthy thicket patches identified as part of the Botanical
Impact Assessment has been excluded from the development area. It also has to be noted
that provision has been made for large areas of Public Open Space along the southern side of
the proposed development area where the natural vegetation can be conserved.
Impact on Heritage resources are considered to be negligible due to the absence of old
structures/buildings or gravesites on the development site.
From an archaeological point of view the proposed development will have no impact on
significant archaeological resources and the correct manner for dealing with archaeological
resources exposed during construction is laid out in the Archaeological Impact Assessment.
Impacts on archaeological resources are considered negligible.
The proposed new development will result in an increase in traffic volumes of the area. This is
considered to be low as the Traffic Impact Assessment make recommendations for best traffic
management. Traffic impact is also unavoidable in terms of township development, thus
mitigation measures needs to be as effective as possible.
The potential impact of installing the external bulk services (sewer line, water line and 1200kl
reservoir) is considered negligible as these services will be installed within already disturbed
areas (i.e. transformed) or servitudes where other services are already accommodated.
Alignment of the water line has been changed through specialist input in order to decrease the
impact on vegetation. A section of the pipeline will aligned along the existing track leading to
the Hartenboskop reservoir. Mossel Bay Municipality confirmed that a servitude can be
registered to accommodate the pipeline.
Providing housing in the Mossel Bay/Sonskynvallei area where there is a known housing need
is considered very high positive.
The visual impact of the proposed development does not constitute a significant impact
considering that amendments were made to the layout to exclude visually sensitive areas,
specify a combination of semi-detached and single erven to reduce the bulk effect, as well as
that the area falls within the urban edge.
The potential of increasing crime and security risks within the established township area is
considered medium negative.
No noise impacts are expected for the operation phase.
Potential erosion during construction phase is considered low negative. By following
mitigation and control measures as indicated in the Environmental Management Programme
this impact can be brought down to very low-negligible.
7. CONCLUSION
The main purpose of the proposed project is to alleviate the need for housing in the greater Mossel
Bay area. The Municipality has identified beneficiaries that are likely to qualify for subsidies and if
approved, these beneficiaries will be further engaged with and assisted with applications for subsidies.
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Cape EAPrac 11 Final Basic Assessment Report
The project is unlikely to result in significant negative environmental impacts whilst creating a
large number of housing opportunities to families. Mitigation measures have been recommended to
manage and reduce impacts to within acceptable limits.
The various specialist studies and project team investigations have all concluded that there is no
fatal flaw in developing the property in the manner proposed. The preferred Alternative 2 is therefore
recommended for approval (Appendix B, layout dated November 2014).
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SECTION A: ACTIVITY INFORMATION
1 PROJECT DESCRIPTION
(a) Is the project a new development? YES NO (b) Provide a detailed description of the development project and associated infrastructure. The Mossel Bay Municipality intends to develop approximately 33.76ha of land adjacent to (south-
west of) the existing Sonskynvallei township into subsidy housing opportunities and associated
township erven. The site is located on Portions 4, 59 & 105 of the Farm Hartenbosch 217, Erf 1853
and Erf 3122, Mossel Bay. The site falls within the urban edge of Mossel Bay.
With regards to bulk infrastructure:
A new 200mm bulk water pipeline from the existing Hartenboskop reservoir will have to be
constructed to service the proposed development with water.
A new internal sewage pump station and rising main is required, which will discharge into the
existing Sonskynvallei pump station with sufficient capacity.
A new 1200kl reservoir to be constructed next to the existing Hartenboskop Reservoir.
These bulk services are assessed as part of this process.
The properties are currently zoned as Agriculture I and Authority, thus rezoning of the property is
necessary. Rezoning will provide for one of the following alternatives (Appendix B – site development
plan):
Alternative 1 (January 2014) Alternative 2 (preferred – November 2014)
686 Residential Zone (subsidy) erven – free-
standing single residential dwellings
616 Residential Zone (subsidy) erven – free-
standing single residential dwellings
2 Transport Zone II erven 2 Transport Zone II erven
14 Public Open Space erven 11 Public Open Space erven
2 Church erven 2 Church erven
1 Crèche erf 1 Crèche erf
1 Business erf 1 Business erf
1 Authority erf 1 Authority erf
Farm Portions 59 & 105 of the Farm Hartenbosch 217 and Erf 1853 are owned by the Mossel Bay
Municipality (the Applicant). Erf 3122 and Portion 4 of the Farm Hartenbosch 217 are owned by the
ATKV (Afrikaanse Taal- en Kultuurvereniging) who have granted the Applicant permission (Annexure
E1) to conduct an environmental impact assessment and develop the property for the goal of subsidy
housing opportunities.
The information below was obtained, unless otherwise indicated, from the Civil Engineering Services
Report (2014), compiled by Louis du Preez from Royal Haskoning DHV, reference Du Preez (2014) –
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Cape EAPrac 13 Final Basic Assessment Report
Annexure G3. Services to the proposed housing development will include the following:
Bulk water supply
The Annual Average Daily Demand (AADD) for the proposed development was estimated to be 600
litres per day for 616 residential units, in total this amounts to 369.6 kilo-litres per day for the entire
proposed housing development. The peak water flow for 616 residential units is estimated to be 17.1 litres per second.
It was confirmed by GLS Consulting that an additional 1200kl reservoir storage is required at the
existing 3500kl Hartenboskop reservoir. The storage in the new reservoir will be shared by the
proposed Sonskynvallei development and other proposed developments in the supply area of the new
reservoir (i.e. Hartenbosch Heuwels extensions). In addition to the increase of the Hartenboskop
reservoir storage capacity, a bulk water supply line will be required from the reservoir to the
proposed site. A 1415m x 200mm pipeline following the gravel track to the reservoir in part, as
well as following within the servitude of an existing 100mm diameter bulk line servicing the
Brandwag township is proposed.
A 10 metre wide corridor route of the pipeline is illustrated in Figure 1 & Figure 2 below. The exact
route of the pipeline within this corridor will be determined during the detailed design phase.
Figure 1: Google Earth image showing the alignment of the proposed new bulk water pipeline to service the proposed development – imagery date September 2013 (Google Earth, 2014). The existing road leading up to the Hartenboskop reservoir from Sonskynvallei is also visible on the image.
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Cape EAPrac 14 Final Basic Assessment Report
Figure 2: Route of the proposed new bulk water line from the Hartenboskop reservoir to the site. The figure also illustrates the route of the proposed new sewer rising main for the proposed development (Du Preez, 2014).
Alignment recommendation by Botanical Specialist
It is proposed that the new bulk water pipeline follow the alignment of the existing pipeline which runs
within a registered servitude (confirmed with engineers) as indicated in Figure 3. This servitude stops
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Cape EAPrac 15 Final Basic Assessment Report
at the boundary of the Remainder of Portion 4 of Farm 217, also indicated in Figure 3. From this point,
the botanical specialist has recommended that the pipeline follow the alignment of the existing road
leading up to the Hartenboskop reservoir as close as possible in order to minimise the impact on
vegetation (road is visible in Figure 3).
―If the trenching of the pipeline is carried out in a sensitive way (ie, by trenching along the
existing road and using a minimum footprint width), it will be possible to lay the pipeline
with very little biodiversity impact.‖ (Coetzee, 2014)
Figure 3: The proposed alignment of the new pipeline is indicated in the figure. The Botanical specialist recommends that where the servitude ends, the pipeline follows the alignment of the existing road leading up to the Hartenboskop reservoir and not as indicated by the blue line.
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Cape EAPrac 16 Final Basic Assessment Report
Figure 4: The pipeline alignment as recommended by the specialists is illustrated. It is recommended that the pipeline follow the alignment of an existing track leading to the Hartenboskop reservoir.
Also taking into account that the existing water servitude runs through a portion that has been flagged
by NFEPA, it was agreed with the Mossel Bay Municipality‟s Technical Manager, Mr Sedick Naidoo
(email correspondence, see Annexure F4) to realign the new water line so that it will follow the existing
gravel track for the portion indicated in the yellow hash line in the above image (a servitude must be
registered along the planned new route for the section where the proposed pipeline follows the road).
This realignment for the specified portion of the water line will ensure compliance with the botanists‟
recommendation. It was confirmed with the land surveyor that the survey of the water pipeline
servitude can be handled when the Phase 3 Erven are surveyed.
Bulk sewage
It is estimated that 80% of the AADD will comprise of sewage flow, this amounts to 500l/d per unit and
308kl/d for 616 units. According to the engineer (RHDHV) officials at the Mossel Bay Municipality have
confirmed that additional flow generated by the proposed housing development can be
accommodated by the existing waste water treatment works once proposed upgrades have been
completed (Annexure E3). The proposed new development will connect to the existing sewerage
network currently servicing Sonskynvallei township via a new sewage pump station with rising main.
Upgrades to segments of the existing network will be determined during detailed design in order to
accommodate additional flow. An internal sewage pump station with rising main will be required for
the proposed development which will discharge into the existing Sonskynvallei pump station which has
sufficient capacity for the additional flow. See Figure 2 for rising main alignment.
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Cape EAPrac 17 Final Basic Assessment Report
Bulk stormwater management
Where possible, the run-off rates for the full spectrum of design storms should not exceed the run-off
rates from the pre-developed site. Minor storm events (1:2 year) will be managed in pipes or open
channels, whereas major storms (1:50 year) will be managed through controlled overland flows and
above-ground attenuation storage. The new stormwater pipe systems will connect to the existing
stormwater network of the adjacent development. Stormwater concentration will be avoided at all
costs. Concrete headwalls with flow dissipaters will be constructed at all outlets, followed by a 0.3m
thick Reno mattress stilling basin for erosion protection and energy dissipation as detailed in
Annexure A of the Civil Services Report.
Access
Access to the proposed development site will be via the existing R328 that runs between Oudtshoorn
and Mossel Bay and existing roads of the Sonskynvallei township. The existing access into
Sonskynvallei Phase 1 will be upgraded according to the recommendations of the TIA.
Solid waste
According to the engineers (RHDHV) officials from Mossel Bay Municipality has confirmed that refuse
generated by the proposed new development will be collected as part of the normal municipal service
and that the landfill site has adequate capacity (Annexure E3).
Above described services refers to bulk services. Internal services are discussed in section 1(d)
below.
(c) List all the activities assessed during the Basic Assessment process:
GN No. R. 544 Activity No(s):
Describe the relevant Basic Assessment Activity(ies) in writing as per Listing Notice 1 (GN No. R. 544)
Describe the portion of the development as per the project description that relates to the applicable listed activity.
11 The construction of (x) buildings and (xi)
infrastructure where such construction
occurs within 32m of a watercourse
measured from the edge of the watercourse.
Development on a section of the
Remainder of Portion 4 of Farm 217 may
fall within 32m from a drainage line that
borders the property to the West (i.e.
infrastructure).
18 The infilling or depositing of any material of
more than 5 cubic metres into, or the
dredging, excavation, removal or moving of
soil, sand, shell grit, pebbles or rock from –
(i) a watercourse
The Civil Services report found that a new
bulk water line that connects to the
Hartenboskop reservoir will have to be
installed. The alternative alignment, as per
the botanist‟s recommendation will avoid
any impact on the NFEPA area.
23 The transformation of undeveloped, vacant
or derelict land to (i) residential, retail,
The planned extension of Sonskynvallei
(Phase 3) will have an approximate
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Cape EAPrac 18 Final Basic Assessment Report
commercial, recreational or institutional use,
inside an urban area, and where the total
area to be transformed is 5ha or more, but
less than 20ha.
footprint area of 14ha (excluding Public
Open Space). Portion 105 is already
transformed and therefore this activity only
applies to the Remainder of Portion 4 and
Portion 59 of Farm 217. GN No. R. 546 Activity No(s):
Describe the relevant Basic Assessment Activity(ies) in writing as per Listing Notice 3 (GN No. R. 546)
Describe the portion of the development as per the project description that relates to the applicable listed activity.
12 The clearance of an area of 300square
meters or more of vegetation where 75% or
more of the vegetative cover constitutes
indigenous vegetation [within any critically
endangered or endangered ecosystem
listed ito NEMBA or prior to the publication
of such a list within an area that has been
identified as critically endangered ito NSBA).
A small section of Remainder Portion 4 of
Farm 217 is designated as CBA (along the
drainage line West of the property). CBA
has not been adopted yet.
The entire development site is indicated
as Grootbrak Dune Strandveld
(endangered in terms of NSBA and
NEMBA but not critically endangered as
per the description of Activity 12).
13 The clearance of an area of 1ha or more of
vegetation where 75% or more of the
vegetative cover constitutes indigenous
vegetation (within critical biodiversity areas
and ecological support areas identified in
systematic biodiversity plans adopted by the
competent authority).
A small section of Remainder Portion 4 of
Farm 217 is designated as CBA (along the
drainage line West of the property). CBA
has not been adopted yet.
14 The clearance of an area of 5ha or more of
vegetation where 75% or more of the
vegetative cover constitutes indigenous
vegetation (in all areas outside urban
areas).
The property falls within the defined urban
edge of Mossel Bay.
16 The construction of (iii) buildings with a
footprint exceeding 10 square metres in size
or (iv) infrastructure covering 10 square
metres or more where such construction
occurs within 32m from the edge of a
watercourse (inside urban areas if zoned
open space, if the area is designated for
conservation use in the SDF and all areas
seawards of the development setback line
or the high water mark where no setback
line exists).
The property falls within the defined urban
area of Hartenbos.
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Cape EAPrac 19 Final Basic Assessment Report
Activity 2 of Listing Notice 3 (R546) relating to the construction of reservoirs was considered for the construction of
the additional reservoir storage. The Hartenboskop reservoir is located within the urban edge of Mossel Bay and
inside an area earmarked as ‗Residential Infill and Expansion Areas‘ in the 2008 Mossel Bay SDF (area is labeled
Hartenbos Heuwels 2 on the Spatial Planning Categories Map). The listed activity is therefore not triggered by the
proposed reservoir construction. If the application is also for activities as per Listing Notice 2 and permission was granted to subject the application to Basic Assessment, also indicate the applicable Listing Notice 2 activities:
GN No. R. 545 Activity No(s):
If permission was granted in terms of Regulation 20, describe the relevant Scoping and EIA Activity(ies) in writing as per Listing Notice 2 (GN No. R. 545)
Describe the portion of the development as per the project description that relates to the applicable listed activity.
Waste management activities in terms of the NEM: WA (Government Gazette No. 32368):
GN No. 718 - Category A Activity No(s): Describe the relevant Category A waste management activity in writing.
Please note: If any waste management activities are applicable, the Listed Waste Management Activities Additional Information Annexure must be completed and attached to this Basic Assessment Report as Appendix I. If the application is also for waste management activities as per Category B and permission was granted to subject the application to Basic Assessment, also indicate the applicable Category B activities:
GN No. 718 – Category B Activity No(s): Describe the relevant Category B waste management activity in writing.
Atmospheric emission activities in terms of the NEM: AQA (Government Gazette No. 33064):
GN No. 248 Activity No(s): Describe the relevant atmospheric emission activity in writing.
(d) Please provide details of all components of the proposed project and attach diagrams (e.g. architectural drawings or perspectives, engineering drawings, process flow charts etc.). Buildings YES NO
Provide brief description:
Approximately 13ha of the proposed site has been identified for the development of ±616 subsidy housing opportunities/erven (preferred alternative) with associated infrastructure. Land uses
include 2 Transport Zone II erven, 11 Public Open Space erven, 2 Church erven, 1 crèche erf and 1
Business zone erf. The entire site is ±33.7ha in size of which ±13ha has been identified for
development, the remainder is indicated for Public Open Space (±20.7ha).
See Appendix B for site development layout. Above describes the preferred development layout
dated November 2014.
Infrastructure (e.g. roads, power and water supply/ storage) YES NO
Provide brief description:
Infrastructure will comprise of the instalment of internal civil services i.e. water supply, foul
sewerage, stormwater management, internal roads, external roads and electrical services. As
mentioned earlier in this report, a 200mm bulk water line will be required from the existing
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Cape EAPrac 20 Final Basic Assessment Report
Hartenboskop reservoir. An additional 1200kl storage reservoir at the Hartenboskop reservoir will
also be required. Also a new sewer pump line with pumpstation must be installed. Refer to section
1(b) and the Civil Services Report (Annexure G3) for a detailed description of the proposed bulk
services upgrades.
Water supply (Du Preez, 2014)
Internal pipes will be sized to cater for the instantaneous peak demand and fire flow. The
network will have a minimum pipe size of 75mm mPVC pipe.
Pipe materials: Mains – mPVC or similar; Erf connections – 20 mm Class 16 Type 5 SABS
533 or Polycop Class 16 JASWIC approved.
Fire flow – fire hydrants to be placed maximum 240m apart.
Foul sewerage (Du Preez, 2014)
Network pipe size will be minimum 160mm in diameter and Erf connections will be 110mm in
diameter.
Pipe material will be solid wall type uPVC.
Pipe cover will be 1.2m below roadways/footways and 0.6m elsewhere.
Stormwater management (Du Preez, 2014)
Minor storms (1:2 year) will be managed through a network of kerb inlets, grid inlets, open channels and below-ground pipes. Major storm events (1:50 year) will be managed
through overland flow via roads and footways, and attenuation storage within public open
spaces and within the road network, as appropriate.
Pipes will have a minimum diameter of 375mm and the pipe material will be concrete or
Spiral HDPE (subject to Municipal approval).
Maximum use of SUDS recommended: open grassed channels (swales), permeable
surfacing (where appropriate), water storage and re-use to reduce stormwater runoff
volumes
Internal roads (Du Preez, 2014)
The internal road surface will be block paving, Cape seal, asphalt or concrete (subject to
Municipal approval at the time of implementation of the project).
The road width will be 3m minimum
Layer works will be dictated by the geotechnical investigation and municipal standards.
External roads (Trafic study) (Maart, 2014; Annexure G6)
A traffic impact assessment (TIA) was conducted to assess the effect of the proposed
development on traffic and the road network in the area, and where mitigation measures will
be necessary. The following recommendations are made in the TIA:
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Mandela Street will be chosen as a single access point to the development and should be
improved by a left turning lane on the eastern approach with a minimum length of 30m.
The Gumpiro Avenue access point onto TR 33/2 to the West of Mandela Street should be
closed off. A request to formalise this access point was raised by the Ward Committee
members during a meeting that took place on 2 July 2014 at the Sonskynvallei Community
Centre regarding the proposed development. It is believed that the safety of the access point
(and possibly formalising it) can be increased significantly if the vegetation inside the road
reserve is cleared. Response on this request from the engineer who conducted the TIA can
be seen in section 11(C) of this report. Also see feedback from Western Cape Government
Department of Transport and Public works below.
The existing pedestrian walkway from Hartenbos to the TR 33/1 - Waboom Street junction
needs to be extended up to the Mandela Street access to the Sonskyn Valley development.
The walkway will be ± 950m long and should be at least 2m wide and to the same standard
as the existing facility.
An internal pedestrian walkway network should also be implemented along Gumpiro
Avenue and along the 13m wide road reserve-roads. These walkways should be at least on
one side of the street and be a minimum of 1.5m wide.
Public transport embayments will be positioned along the 13m wide road reserve – roads
with the objective for commuters not to walk more than 500m to the pick-up or drop-off point.
On 15 October 2014 this office received comment from the Western Cape Government Department
Transport and Public Works stating the following:
- This branch will not be opposed to the issuing of an Environmental Authorisation, provided
that a Land Use Planning Ordinance (LUPO) application is submitted via the Local Authority
to this Branch.
- At this stage this Branch can state the following:
o It accepts the motivation of the Traffic Impact Study
o The following accesses will have to be closed:
Off Trunk Road 33 section 2 at ±km0.88 LHS (waste disposal)
Off Trunk Road 33 section 2 at ±km0.94 LHS (Gumpiro Avenue)
- Mandela Street off Trunk Road 33 section 2 at ±km0.94 LHS will have to be upgraded as per
SMEC‟s recommendation (Traffic Impact Assessment).
- The proposed layout must be amended in order to construct another access when required,
onto Trunk Road 33 section 2 at ±km1.78 LHS (opposite the mine).
Electricity (CVW Electrical, 2014; Annexure G4)
Electricity will be supplied by Mossel Bay Municipality.
Supply will be provided from the newly built 66/11kV 20MVA Substation situated
approximately 1km east of the proposed development.
Distribution on the property will be an 11000/420V underground cable system, which will
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Cape EAPrac 22 Final Basic Assessment Report
have no visual impact on the environment. High Voltage cables will be installed at a minimum
depth of 1000mm and low Voltage cables at a minimum depth of 600mm from finished
ground level.
The Municipality will install energy efficient street lighting, 57W Compact Fluorescent‟s on
5, 4m poles.
Telephone network will be supplied by Telkom, whose cables will be overhead. Processing activities (e.g. manufacturing, storage, distribution) YES NO
Provide brief description:
Storage facilities for raw materials and products (e.g. volume and substances to be stored)
Provide brief description YES NO
Storage and treatment facilities for solid waste and effluent generated by the project Yes NO
Provide brief description
Other activities (e.g. water abstraction activities, crop planting activities) Yes NO
Provide brief description
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1.1 INFRASTRUCTURE DESCRIPTION This section describes infrastructure upgrades proposed for Phase 3 of Sonskynvallei. It takes into account infrastructure upgrades recommended in the Civil Services Report (Du Preez, 2014), the Traffic Impact Assessment (Maart, 2014) and comment received by the Western Cape Government Department of Transport and Public Works (received 15 Oct 14, see section A 3(C) of this report). Please note, the numbers of the descriptions following below correspond with the numbers on the map in Figure 4. The descriptions must be read whilst referring to the map.
Figure 5: Map illustrating the location and short description of infrastructure upgrades proposed for Phase 3 of Sonskynvallei Housing. The map does not include the proposed new water pipeline and reservoir upgrade as these are described earlier in this report.
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1) The TIA recommends that “The existing pedestrian walkway from Hartenbos to the TR 33/1 -
Waboom Street junction needs to be extended up to the Mandela Street access to the
Sonskyn Valley development. The walkway will be ± 950m long and should be at least 2m
wide and to the same standard as the existing facility.” (Annexure G7)
On 1 October 2014 a site visit was conducted to investigate the vegetation along the route
described above and to establish whether any protected trees occur along the proposed
walkway route. As illustrated in the figures below, the proposed walkway will have no negative
impact on indigenous vegetation, whether it is constructed along the northern or southern side
of the R328. As a whole the environmental impact of the walkway can be described as
negligible, with a positive social and safety impact. It must be ensured that construction
activities only take place within demarcated areas as to not negatively impact vegetation
further away from the road and outside the road reserve.
Figure 6: Vegetation along the southern section of the R328 where the walkway is proposed, note that the vegetation directly adjacent to the road consist of grasses. At this particular point a milkwood (indicated by arrow) is within close proximity of the road. It is anticipated that if construction occurs within demarcated areas, this milkwood will not be affected. In the background, where the white bakkie is, is the Mandela Street turnoff to Sonskynvallei. The Department Transport and Public Works have recommended that the turnoff in the foreground be closed. This photo was taken looking in a north easterly direction along the R328.
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Figure 7: This photo was taken from same position as Figure 6 looking in a south easterly direction towards Hartenbos along the R328. Vegetation directly adjacent to the road consists of grasses and there are no protected trees found along this stretch up to Waboom Street (where walkway is proposed to stop). Reeds seen in this photo is associated with stormwater runoff from the road
Figure 8: The photo was taken looking back towards Sonskynvallei at the approximate halfway mark between Mandela and Waboom Street. Vegetation is sparse and consists of grasses.
Figure 9: This photo was taken at the same location as Figure 7, looking in the opposite direction, towards Hartenbos. The turnoff to Waboom Street can be seen in the background. Impact on vegetation along this section is also considered to be negligible.
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2) Comment received from the Western Cape Government Department of Transport and Public
Works on 15 October 2014 stated that ―the following access will have to be closed: Off trunk
Road 33 section 2 at ±km0.88 LHS (waste disposal).‖ This access point (Figure 10) is located
approximately 50m from the Mandela Street turnoff (proposed as single access point for
Sonskynvallei) and acts as a second access point to the waste disposal (Figure 11). Future
access to the waste disposal site will be via Mandela Street.
Figure 10: The access point referred to as „waste disposal‟ in comment received from the Department of Transport and Public Works which the Department to be closed off. The waste disposal site can be seen in the background, behind the white wall
Figure 11: The waste disposal site at Sonskynvallei, which will be accessed via Mandela Street in future.
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3) The TIA recommended that “Mandela Street will be chosen as a single access point to the
development and should be improved by a left turning lane on the eastern approach with a
minimum length of 30m.The Gumpiro Avenue access point onto TR 33/2 to the West of
Mandela Street should be closed off.” Impact on vegetation if the proposed left turning lane
were to be constructed is considered negligible Figure 12.
Figure 12: This photo was taken from the „waste disposal‟ access point (to be closed off) looking towards the Mandela Street access point (seen in the background where the bakkie is) situated approximately 50m from where this photo was taken. There will therefore be ample space to construct a left turning lane with minimum length of 30m. From the figure it is clear that the impact on vegetation is negligible.
4) Comment received from the Western Cape Government Department of Transport and Public
Works on 15 October 2014 stated that ―the following access will have to be closed: Off Trunk
Road 33 section 2 at ±km1.59 LHS (Gumpiro Avenue).‖ Prior to the comment received by the
Department, the local Ward Committee members requested that this access point remain and
be formalised as a second access point to Sonskynvallei (TIA recommends it be closed for
safety reasons). Correspondence highlighting the committees request was sent to the Dept.
on 14 July 2014.
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Figure 13: The Gumpiro Avenue access point. It was recommended by the TIA and Dept. Transport and Public Works that this access point be closed. This photo was taken in a westerly direction, showing the R328 to Oudtshoorn on the right and the clinic and community centre on the left in the background.
Figure 14: The two photos were taken from the existing Gumpiro Avenue access point (to be closed). The photo on the left is taken in the direction of Oudtshoorn and the photo on the right in the direction of Hartenbos.
5) Comment received from the Western Cape Government Department of Transport and Public
Works on 15 October 2014 stated that ―the proposed layout must be amended in order to be
able to construct another access when required, onto Trunk Road 33 section 2 at ±km1.78
LHS (opposite the mine). Development has been excluded from this point where, according to
the above comment, a future access point may possibly be constructed. The botanical
specialist identified this area as being sensitive and development was subsequently excluded
here. Despite the sensitive vegetation, the height difference between the road and the
development site at this particular place is quite high (Figure 15) and may pose a challenge to
future road construction. This location can be earmarked as a possible future access point and
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will have to go through the appropriate procedure should it be decided an access point is
required here.
Figure 15: The height difference between the road and site is illustrated in this picture. In the foreground is an access point for a PetroSA water line indicated in the site development plan. No development will take place on the water line servitude
6) The Civil Services Report states that a new pump station will have to be constructed at this
point. The pump station will fall within the greater footprint of the housing development. The
figure below illustrates the vegetation at this point.
Figure 16: It is proposed that the new pump station be constructed on the grassed area on the left of this photo. This area was assessed by the botanical specialist and found suitable for development. Areas seen on the right
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hand side of this photo has been excluded from the development area as it has been identified as sensitive and conservation worthy by the specialist
7) The Civil Services Report indicated that a new sewer rising main will have to be constructed.
The line will travel from the existing Sonskynvallei pump station to the proposed new pump
station described in point „6‟ above. After a site visit it was found that the most suitable
alignment for the rising main, with least vegetative impact, would be for the rising main to be
aligned inside the road reserve of Gumpiro Avenue. This was discussed with the engineer at
Royal Haskoning DHV and confirmed to be a good recommendation. Below are images
illustrating the vegetation along the proposed route of the new sewer rising main.
Figure 17: The new rising main will start at the existing Sonskynvallei pump station and travel in a north westerly direction (photo on the right) toward the location of the new pump station.
Figure 18: The vegetation along Gumpiro Avenue road reserve where rising main is proposed to be installed. The Sonskynvallei pump station is visible in the background
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Figure 19: The vegetation along Gumpiro Avenue is illustrated looking in a north westerly direction towards the current Gumpiro Avenue access point. The rising main is proposed to be installed on the left of the fence seen in this photo
Figure 20: Vegetation along the rising main route in the northern corner of the proposed development site/north of the clinic. This vegetation was assessed as part of the botanical specialist assessment and not found to be sensitive
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Figure 21: The photo shows, from the left, the R328, stormwater channel next to the road and the Gumpiro Avenue road reserve. Sonskynvallei pump station is visible in the background, along the road reserve. It would be impractical to align the sewer rising main in the stormwater channel next to the road, therefore the Gumpiro Avenue road reserve is recommended to be more suitable.
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2. PHYSICAL SIZE OF THE ACTIVITY
Size of the property: (a) Indicate the size of the property (cadastral unit) on which the activity is to be undertaken.
All properties are located in the Mossel Bay District Total: ±278.4ha
Portion 4 of the Farm Hartenbosch 217 ±43.1ha Portion 59 of the Farm Hartenbosch 217 ±16.7ha Portion 105 of the Farm Hartenbosch 217 ±6.4ha Erf 1853 ±151.7ha Erf 3122 ±60.5ha
Size of the facility: (b) Indicate the size of the facility (development area) on which the activity is to be undertaken.
Total development site – includes areas identified for Public Open
Space. ±33.76ha
Size of the activity: (c) Indicate the physical size (footprint) of the activity together with its associated infrastructure:
Excluding Public Open Space. ±13ha
(d) Indicate the physical size (footprint) of the activity:
Only development of Residential Zone I ±8.8ha
(e) Indicate the physical size (footprint) of the associated infrastructure:
Only Transport Zone II. 42 310m2
and, for linear activities:
Length of the activity: (f) Indicate the length of the activity:
New bulk water pipeline from Hartenboskop reservoir to proposed phase 3 housing development at Sonskynvallei
±1.4km
New Rising main sewer line ±540m
3. SITE ACCESS
(a) Is there an existing access road? YES NO
(b) If no, what is the distance over which a new access road will be built? m
(c) Describe the type of access road planned:
Access to the site would be via the existing R328 and Mandela Road as recommended and
indicated in the Traffic Impact Assessment (TIA) (Maart, 2014) - Annexure G6.
As listed in section 1(b) above the following recommendations are made in the TIA:
Mandela Street will be chosen as a single access point to the development and should be
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improved by a left turning lane on the eastern approach with a minimum length of 30m.
The Gumpiro Avenue access point onto TR 33/2 to the West of Mandela Street should be
closed off.
The existing pedestrian walkway from Hartenbos to the TR 33/1 - Waboom Street junction
needs to be extended up to the Mandela Street access to the Sonskyn Valley development.
The walkway will be ± 950m long and should be at least 2m wide and to the same standard
as the existing facility.
An internal pedestrian walkway network should also be implemented along Gumpiro Avenue
and along the 13m wide road reserve-roads. These walkways should be at least on one side
of the street and be a minimum of 1.5m wide.
Public transport embayments will be positioned along the 13m wide road reserve – roads
with the objective for commuters not to walk more than 500m to the pick-up or drop-off point.
On 15 October 2014 this office received comment from the Western Cape Government Department
Transport and Public Works stating the following:
- This branch will not be opposed to the issuing of an Environmental Authorisation, provided
that a Land Use Planning Ordinance (LUPO) application is submitted via the Local Authority
to this Branch.
- At this stage this Branch can state the following:
o It accepts the motivation of the Traffic Impact Study
o The following accesses will have to be closed:
Off Trunk Road 33 section 2 at ±km0.88 LHS (waste disposal)
Off Trunk Road 33 section 2 at ±km0.94 LHS (Gumpiro Avenue)
- Mandela Street off Trunk Road 33 section 2 at ±km0.94 LHS will have to be upgraded as per
SMEC‟s recommendation (Traffic Impact Assessment).
- The proposed layout must be amended in order to construct another access when required,
onto Trunk Road 33 section 2 at ±km1.78 LHS (opposite the mine). Please Note: indicate the position of the proposed access road on the site plan.
4. DESCRIPTION OF THE PROPERTY ON WHICH THE ACTIVITY IS TO BE UNDERTAKEN AND THE LOCATION OF THE ACTIVITY ON THE PROPERTY
(a) Provide a description of the property on which the activity is to be undertaken and the location of the activity on the property. The development site can be described as an undeveloped area located between a housing suburb
to the east (existing Sonskynvallei township Phase 1), brickworks to the west, agricultural land to the
north and a „natural‟ area to the south. Five (5) properties make up the development site. In total
these properties covers an area of ±278ha.
The proposed development will however have an approximate footprint of 33.76ha (including
Public Open Space). The development will consist of a housing component, a new bulk water
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supply line from the Hartenboskop reservoir to the new development and the construction of
additional 1200kl reservoir at the Hartenboskop reservoir1.
Housing
The housing activity will have an approximate footprint of 13ha (with associated infrastructure) and is
located on the northern section of the development site, adjacent to the existing Sonskynvallei
township. The development site can be described as a natural area and is unrestrictedly connected
to an extensive area of similar natural vegetation to the south (Coetzee, 2014).
In terms of topography the development is located on a northerly facing slope where it reaches the
top of a hill and then slopes southward to the abovementioned natural vegetation. The location of the
housing component of the activity on the property is illustrated in the Figure 22 below.
Figure 22: Area of the proposed site that has been identified for housing development (location of the housing activity on the property) i.e. outlined in yellow is the proposed area where the houses will physically be built, Public Open Space is excluded.
Infrastructure
The proposed new 200mm bulk water line will start at the existing Hartenboskop reservoir and cross
Erf 3122, Erf 1853, Remainder of Portion 4 of Farm 217 and Portion 105 of Farm 217. The initial
1 Activity 2 of Listing Notice 3 (R546) relating to the construction of reservoirs was considered for the
construction of the additional reservoir storage. The Hartenboskop reservoir is located within the urban edge of Mossel Bay and inside an area earmarked as „Residential Infill and Expansion Areas‟ in the 2008 Mossel Bay SDF (area is labeled Hartenbos Heuwels 2 on the Spatial Planning Categories Map). The listed activity is therefore not triggered by the proposed reservoir construction.
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proposal by the engineers was to install this new water line within the existing water line servitude.
This servitude however crosses an area flagged ito NFEPA and it has since been recommended by
the botanical specialist that a portion of the pipeline route be amended to follow the existing gravel
track and in doing so avoid the NFEPA area completely (confirmed with Mossel Bay Municipality, see
Annexure F4). It is proposed that the pipeline be installed adjacent to an existing water line (thus
follow the same alignment) for 2/3 of the servitude route and will be approximately 1.4km in length
(exact length of the pipeline will be determined by the engineers during detailed design). Furthermore
the Botanical Specialist described the location of the pipeline as follows:
“A part (roughly one-third) of the pipeline route lies through the existing residential area
and along the Hartenbos/Oudtshoorn tarred road and its construction or upgrading in
this area will thus have no impact on any area of natural vegetation. The three
remaining sections consist largely of grassy renosterveld and the upper pipeline route
lies all along a ridge. There are no sensitive habitats (like wetlands, seeps, thicket
patches, quartz patches or limestone patches or even patches of mature fynbos) along
the route.” (Coetzee, 2014)
Figure 23: Proposed alignment of the new bulk water pipeline. The pipeline should however avoid the area indicated by NFEPA as being sensitive, therefore it must be realigned to follow the existing gravel track instead.
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Figure 24: Proposed new pipeline alignment as recommended by specialists. The proposed new alignment means a section of the pipeline will be aligned an along an existing track leading to the Hartenboskop reservoir.
The new pump sewer line with pumpstation will be installed next to the R328. The engineers from
RHDHV have confirmed that the exact alignment of the sewer line will be determined during detailed
design. It is also during this stage that the engineers will determine if the sewer line will be inside the
road reserve or outside. If inside, the engineers will follow the appropriate steps and correspondence
with the Roads Authority.
Following a site visit (1 Oct 2014), it is recommended that the sewer line be aligned within the road
reserve of Gumpiro Avenue as illustrated and described in Section A – 1.1 (Infrastructure
Description). The alignment will have the least vegetative impact, it is also more practical as there is
a stormwater channel (Figure 21) adjacent to the R328 and aligning the sewer main in this channel is
unfeasible. This was discussed with the engineer at RHDHV and confirmed to be a good
recommendation.
It was confirmed by GLS Consulting that an additional 1200kl reservoir storage is required at the
existing 3500kl Hartenboskop reservoir (Du Preez, 2014). The storage in the new reservoir will be
shared by the proposed Sonskynvallei development and other proposed developments in the supply
area of the new reservoir. The photographs below show the existing Hartenboskop reservoir and the
vegetation around it.
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Figure 25: The existing Hartenboskop reservoir is seen in the background. Vegetation around the site comprises a mixture of indigenous and alien plants. The botanical specialist described the vegetation close (and around) the reservoir as „somewhat transformed‟. The fence around the reservoir site has been largely destroyed and vandalised. The photo was taken in a westerly direction.
Figure 26: Vegetation at the Hartenboskop reservoir. Photo taken from the reservoir to the where Figure 25
was taken from, in a north-easterly direction.
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(b) Please provide a location map (see below) as appendix a to this report which shows the location of the property and the location of the activity on the property; as well as a site map (see below) as appendix b to this report; and if applicable all alternative properties and locations.
Locality map:
The scale of the locality map must be at least 1:50 000. For linear activities of more than 25 kilometres, a
smaller scale e.g. 1:250 000 can be used. The scale must be indicated on the map. The map must indicate the
following:
an accurate indication of the project site position as well as the positions of the alternative sites, if any; road names or numbers of all the major roads as well as the roads that provide access to the site(s) a north arrow; a legend; the prevailing wind direction (during November to April and during May to October); and GPS co-ordinates (Indicate the position of the activity using the latitude and longitude of the centre point
of the site for each alternative site. The co-ordinates should be in degrees and decimal minutes. The minutes should have at least three decimals to ensure adequate accuracy. The projection that must be used in all cases is the WGS84 spheroid in a national or local projection).
See Appendix A for location and topographical map.
Site Plan:
Detailed site plan(s) must be prepared for each alternative site or alternative activity. The site plan must contain or conform to the following: The detailed site plan must be at a scale preferably at a scale of 1:500 or at an appropriate scale. The
scale must be indicated on the plan. The property boundaries and numbers of all the properties within 50m of the site must be indicated on the
site plan. The current land use (not zoning) as well as the land use zoning of each of the adjoining properties must
be indicated on the site plan. The position of each element of the application as well as any other structures on the site must be
indicated on the site plan. Services, including electricity supply cables (indicate above or underground), water supply pipelines,
boreholes, sewage pipelines, storm water infrastructure and access roads that will form part of the development must be indicated on the site plan.
Servitudes indicating the purpose of the servitude must be indicated on the site plan. Sensitive environmental elements within 100m of the site must be included on the site plan, including (but
not limited to): o Rivers. o Flood lines (i.e. 1:10, 1:50, year and 32 meter set back line from the banks of a river/stream). o Ridges. o Cultural and historical features. o Areas with indigenous vegetation (even if it is degraded or infested with alien species).
Whenever the slope of the site exceeds 1:10, then a contour map of the site must be submitted. See Appendix B for Site Plans – Preferred layout is dated November 2014.
(c) For a linear activity, please also provide a description of the route. The proposed bulk water pipeline that forms part of this Basic Assessment report will:
Travel from the existing Hartenboskop reservoir to the proposed housing development in a
mainly eastern and north-eastern direction;
Follow the alignment of an existing road leading up to the reservoir (as recommended by the
Botanical Specialist);
Where the pipeline reaches the border of RE Portion 4 of Farm 217 it will follow the alignment
of an existing water pipeline inside a registered servitude (Figure 3) towards the Sonskynvallei
Township;
It then travels almost in straight line towards Gumpiro Avenue.
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Figure 27: Alignment of proposed bulk water pipeline to service the proposed development. The pipeline will start at the existing Hartenboskop reservoir and be approximately 1.4km in length – imagery date September 2013 (Google Earth, 2014). The proposed new sewer line will run along the northern boundary of the proposed development,
adjacent to the R328. The engineers at RHDHV confirmed the exact alignment of the sewer line, and
whether it will be inside or outside the road reserve, will be determined during detailed design. It is
recommended that the sewer line be aligned inside the Gumpiro Avenue road reserve. The sewer line
will start at the proposed new sewage pump station at the northern corner of Portion 105 of Farm 217
(north of the rugby field). It will then travel in an easterly direction to the existing sewage pump station
(Figure 17) at the corner of Jansen Avenue (Figure 2 & Annexure G3).
It must be noted that for the purpose of this environmental investigation both the sewer and water
pipeline routes were assessed as a 10 metre wide corridor with a centre coordinate (see below). The
reason for this approach is to allow some flexibility for the final alignment which depends on the detail
engineering design that is only done post the environmental process.
The corridor width for each of these features must therefore be considered and approved instead of a
specific line only.
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Indicate the position of the activity using the latitude and longitude of the centre point of the site. The co-ordinates must be in degrees, minutes and seconds. The minutes should be given to at least three decimals to ensure adequate accuracy. The projection that must be used in all cases is the WGS84 spheroid in a national or local projection.
Latitude (S): Longitude (E):
34o 07„ 03.90“ 22o 04„ 56.94“
(d) or: For linear activities: New bulk water pipeline Latitude (S): Longitude (E):
Starting point of the activity 34o 07„ 24.79“ 22o 05„ 08.03“ Middle point of the activity 34o 07„ 11.95“ 22o 04„ 57.96“ End point of the activity 34o 06„ 52.30“ 22o 05„ 03.12“
The following are the coordinates for the new sewer line:
Start at new sewage pump station - 34˚06‟50.34”S 22˚04‟57.33”E
End at existing sewage pump station - 34˚06‟55.28”S 22˚05‟16.23”E
Coordinates are approximate and forms the centre line of a 10 metre wide corridor. The pipeline(s)
should be installed within this 10 metre wide corridor. Please Note: For linear activities that are longer than 500m, please provide and addendum with co-ordinates taken every 100 meters along the route. Below are coordinates of the proposed water pipeline taken every 100m and at every
directional changes, as per the alignment illustrated in Figure 27. Coordinates are approximate and forms the centre line of a 10 metre wide corridor. The pipeline should be installed within
this 10 metre wide corridor
Table 1: Coordinates of the proposed water pipeline from the existing Hartenboskop reservoir to the proposed Phase of the Sonskynvallei housing development.
Distance (metres) SOUTH EAST
0 start
Hartenboskop reservoir 34˚07‟24.79” 22˚05‟08.03”
23 34˚07‟25.05” 22˚05‟07.17”
46 34˚07‟24.75” 22˚05‟06.35”
92 34˚07‟23.24” 22˚05‟06.32”
186 34˚07‟22.77” 22˚05‟02.68”
286 34˚07‟20.74” 22˚04‟59.71”
307 34˚07‟20.29” 22˚04‟59.08”
407 34˚07‟18.80” 22˚04‟55.60”
410 34˚07‟18.75” 22˚04‟55.47”
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493 34˚07‟16.36” 22˚04‟54.01”
593 34˚07‟13.73” 22˚04‟56.35”
693 34˚07‟13.75” 22˚04‟55.34”
738 34˚07‟09.68” 22˚04‟58.77”
834 34˚07‟06.94” 22˚04‟57.12”
934 34˚07‟03.85” 22˚04‟58.48”
1034 34˚07‟00.81” 22˚04‟59.84”
1134 34˚06‟57.76” 22˚05‟01.12”
1234 34˚06‟54.71” 22˚05‟02.51”
1300 34˚06‟52.30” 22˚05‟03.12”
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5. SITE PHOTOGRAPHS
Colour photographs of the site and its surroundings (taken of the site and from the site) with a description of each photograph. The vantage points from which the photographs were taken must be indicated on the site plan, or locality plan as applicable. If available, please also provide a recent aerial photograph. Photographs must be attached as Appendix C to this report. It should be supplemented with additional photographs of relevant features on the site. Date of photographs must be included. Please note that the above requirements must be duplicated for all alternative sites.
See Appendix C for Site Photographs
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SECTION B: DESCRIPTION OF RECEIVING ENVIRONMENT
1. SITE/AREA DESCRIPTION
For linear activities (pipelines, etc.) as well as activities that cover very large sites, it may be necessary to complete copies of this section for each part of the site that has a significantly different environment. In such cases please complete copies of Section B and indicate the area which is covered by each copy No. on the Site Plan.
2. GRADIENT OF THE SITE
Indicate the general gradient of the sites (highlight the appropriate box).
Figure 28: Slope (in degrees) of the proposed development area is indicated in the figure. Map was generated on CapeFarmMapper – Western Cape Department of Agriculture (CapeFarmMapper, 2014)
3. LOCATION IN LANDSCAPE
(a) Indicate the landform(s) that best describes the site (highlight the appropriate box(es).
Ridgeline Plateau Side slope of hill/mountain
Closed valley
Open valley Plain
Undulating plain/low hills Dune Sea-
front
(b) Please provide a description of the location in the landscape. The site forms part of an open/undulating hill landscape that slope northwards towards the R328 that
Flat Flatter than 1:10 1:10 – 1:4 Steeper than 1:4
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connect Hartenbos and Oudtshoorn. The figures below illustrate the location of the site in the
landscape.
Figure 29: Location of the development site in the landscape indicating the R328 between Hartenbos and Oudtshoorn (Google Earth, 2014).
Figure 30: Contour plan (5m) of the proposed Sonskynvallei development site. The figure illustrates the proposed new bulk water pipeline alignment as recommended by specialists (line) and the proposed
Development Site
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development site (polygon). Please note that the area identified for housing development does not comprise the entire development site as indicated in this figure, refer to Appendix B – Development layout. Map was generated on CapeFarmMapper – Department of Agriculture (CapeFarmMapper, 2014)
4. GROUNDWATER, SOIL AND GEOLOGICAL STABILITY OF THE SITE
(a) Is the site(s) located on or near any of the following (highlight the appropriate boxes)?
Shallow water table (less than 1.5m deep) YES NO UNSURE Seasonally wet soils (often close to water bodies) YES NO UNSURE Unstable rocky slopes or steep slopes with loose soil YES NO UNSURE Dispersive soils (soils that dissolve in water) YES NO UNSURE Soils with high clay content YES NO UNSURE Any other unstable soil or geological feature YES NO UNSURE An area sensitive to erosion YES NO UNSURE An area adjacent to or above an aquifer. YES NO UNSURE An area within 100m of the source of surface water YES NO UNSURE
(b) If any of the answers to the above are “YES” or “unsure”, specialist input may be requested by the Department.
(Information in respect of the above will often be available at the planning sections of local authorities. Where it exists, the
1:50 000 scale Regional Geotechnical Maps prepared by Geological Survey may also be used).
(c) Please indicate the type of geological formation underlying the site.
Granite Shale Sandstone Quartzite Dolomite Dolorite Other
(describe)
Please provide a description.
The geological information below was obtained from the Agricultural Geo-Referenced Information
System‘s (AGIS) using the „Comprehensive Atlas‟ (AGIS, 2014).
The Geology of the proposed development site is described on AGIS as: “Mainly conglomerate,
sandstone, siltstone and mudstone of the Enon Formation, Uitenhage Group, with quartzitic sandstone
of the Table Mountain Group, Cape Supergroup.”
In terms of soil the following information was obtained from AGIS:
Generalized Soil Pattern
Soils with a marked clay accumulation, strongly structured and a non-reddish colour. They may occur
associated with one or more of vertic, melanic and plinthic soils.
Wind Erosion
Indicated as Loamy Sands Sub-Dominant which is classified as moderately susceptible to wind
erosion.
Water Erosion
Land with moderate to high water or wind erosion hazard. Generally moderately to strongly sloping
land. Soils have low to moderate erodibility.
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5. SURFACE WATER
(a) Indicate the surface water present on and or adjacent to the site and alternative sites (highlight the appropriate boxes)?
Perennial River YES NO UNSURE
Non-Perennial River YES NO UNSURE
Permanent Wetland YES NO UNSURE
Seasonal Wetland YES NO UNSURE
Artificial Wetland YES NO UNSURE
Estuarine / Lagoonal wetland YES NO UNSURE
(b) Please provide a description. Set within an otherwise undulating landscape, the site is found on the northern slope of one of these
undulating hills. Surface water adjacent to the site consists of drainage lines that flow towards the
Hartenbos River (located approximately 260m north/north-east of the nearest point of the proposed
Phase 3 development). The preferred housing with associated infrastructure of the development
will not be within 32m of such drainage lines.
6. BIODIVERSITY
Please note: The Department may request specialist input/studies depending on the nature of the biodiversity occurring on the site and potential impact(s) of the proposed activity/ies. To assist with the identification of the biodiversity occurring on site and the ecosystem status consult http://bgis.sanbi.org or [email protected]. Information is also available on compact disc (cd) from the Biodiversity-GIS Unit, Ph (021) 799 8698. This information may be updated from time to time and it is the applicant/ EAP‟s responsibility to ensure that the latest version is used. A map of the relevant biodiversity information (including an indication of the habitat conditions as per (b) below) and must be provided as an overlay map to the property/site plan as Appendix D to this report. (a) Highlight the applicable biodiversity planning categories of all areas on site and indicate the reason(s) provided in the
biodiversity plan for the selection of the specific area as part of the specific category).
Systematic Biodiversity Planning Category If CBA or ESA, indicate the reason(s) for its selection in biodiversity plan
Critical Biodiversity Area (CBA)
Ecological
Support
Area (ESA)
Other
Natural
Area (ONA)
No Natural
Area
Remaining
(NNR)
A small portion of the development site falls within a
CBA along the western border and a larger portion
(particularly around the rugby field) is indicated as
CBA Buffer.
From the CBA map it appears that the proposed new
bulk water pipeline will go through a small area
indicated as a CBA Terrestrial. (Coetzee (2014)
stated that there are no sensitive areas within the
route of the pipeline.
See Appendic D for CBA Map.
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(b) Highlight and describe the habitat condition on site. Habitat condition described below refers to the proposed development site (Including Public Open Space).
Habitat Condition
Percentage of habitat condition class (adding up
to 100%)
Description and additional Comments and Observations (including additional insight into condition, e.g. poor land
management practises, presence of quarries, grazing/harvesting regimes etc).
Natural 10%
Areas of true thicket occur along the western border of the proposed development site. This is the only area that can be described as „natural‟ as too frequent fires have changed the remainder of the site from its natural state. Less intact thicket patches also occur in the proposed development area.
Near Natural
(includes areas with low to
moderate level of alien
invasive plants)
60%
The majority of the site can be described as „near-natural‟ as the vegetation on site is described on a fine scale as Herbertsdale Renoster Thicket which is characterised by small patches of thicket occurring in a matrix of Renosterveld (Coetzee, 2014). The Renosterveld component has been somewhat degraded as a result of too frequent fires.
Degraded
(includes areas heavily
invaded by alien plants) 10%
Degraded areas are found around (fringes) transformed areas. This is areas in the north and north-east of the rugby field as well as around the Hartenboskop reservoir. Many areas of Renosterveld have experienced too frequent fires and are dominated by grasses.
Transformed
(includes cultivation, dams,
urban, plantation, roads, etc) 20%
The north and north-eastern corner of the proposed development site around the rugby field, clinic and community centre has been completely transformed. Also the area that immediately surrounds the Hartenboskop reservoir.
(c) Complete the table to indicate:
(i) the type of vegetation, including its ecosystem status, present on the site; and
(ii) whether an aquatic ecosystem is present on site.
(d) Please provide a description of the vegetation type and/or aquatic ecosystem present on site, including any important
biodiversity features/information identified on site (e.g. threatened species and special habitats)
According to SANBI BGIS the entire site is described as Groot Brak Dune Strandveld and classified
as ‘Endangered’ in terms of ecosystem status, and ‘not protected’ in terms of protection status. This
Terrestrial Ecosystems Aquatic Ecosystems
Ecosystem threat status as per the
National Environmental Management:
Biodiversity Act (Act No. 10 of 2004)
Critical Wetland (including rivers,
depressions, channelled and
unchanneled wetlands, flats,
seeps pans, and artificial
wetlands)
Estuary Coastline Endangered
Vulnerable
Least Threatened YES NO UNSURE YES NO YES NO
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vegetation type is associated with flat undulating landscapes and steep coastal slopes. It is mostly
underlain by clastic sedimentary rocks of the Kirkwood formation, however towards the east quartzite,
schist and phyllite of the Kaaimans Group and Cape Granite are also present. The largest area
covering of this vegetation type is north of Mossel Bay. (Rebelo et al. 2006)
At a finer scale the vegetation has been described as Herbertsdale Renoster Thicket which is
characterised by small thicket clumps occurring in a matrix of Renosterveld. The Renosterveld
component of the vegetation is very grassy in the areas most recently burnt. True thicket occurs west
of the rugby field (Coetzee, 2014). Coetzee (2014) has recommended that the larger thicket area
along the western border of the proposed development site be excluded from the development area
as it can connect to thicket on the neighbouring property (labelled „1 & 2‟ in Figure 31). Other thicket
patches within the development area are isolated and not considered worthy of
conservation/preservation effort (labelled „3‟ in Figure 31). This is reflected in the Site Development
Plan of the preferred alternative (Appendix B, dated November 2014).
Figure 31: The figure above is from Coetzee (2014), and illustrates areas of the proposed
development site (yellow) in terms of their sensitivity. Areas 1 -3 indicate thicket vegetation and 4
indicate an area that has been mostly transformed.
In general the site can be described as being in fair condition with some thicket patches occurring
within the Renosterveld. The vegetation of the proposed development site can be summarised as
follows:
- The vegetation of the development area is classified as Herbertsdale Renoster Thicket –
characterised by small thicket clumps within a matrix of Renosterveld
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- Areas north and north-east of the rugby field have been mostly transformed;
- True thicket occur along the north-western boundary of the development site;
- Isolated thicket patches occur within the development site;
- Renosterveld areas exposed to too frequent fires are grass dominated.
7. LAND USE OF THE SITE
Please note: The Department may request specialist input/studies depending on the nature of the land use character of the area and potential impact(s) of the proposed activity/ies.
Untransformed area Low density residential Medium density residential
High density residential Informal residential
Retail Commercial & warehousing Light industrial Medium industrial Heavy industrial
Power station Office/consulting room Military or police
base/station/compound
Casino/entertainment complex
Tourism & Hospitality facility
Open cast mine Underground mine Spoil heap or slimes dam
Quarry, sand or borrow pit Dam or reservoir
Hospital/medical center (Clinic)
School (crèche) Tertiary education facility
Church Old age home
Sewage treatment plant
Train station or shunting yard Railway line Major road (4 lanes or
more) Airport
Harbour Sport facilities
(rugby field and netball courts)
Golf course Polo fields Filling station
Landfill or waste treatment site Plantation Agriculture River, stream or
wetland Nature conservation
area Mountain, koppie or
ridge Museum Historical building Graveyard Archeological site
Other land uses (describe):
(a) Please provide a description. In overall context the land use of the site can be described as natural/undeveloped. There is also a
rugby field, netball court (under construction), crèche and clinic on the site. These facilities are
currently used by people from the existing Sonskynvallei township.
Phase 2 of Sonskynvallei has already been approved with services and this phase will be
implemented before Phase 3 is implemented.
The proposed development, Phase 3, will in-part be constructed around the rugby field, crèche and
clinic. Most of the development will be constructed on an area described as natural.
8. LAND USE CHARACTER OF SURROUNDING AREA
(a) Highlight the current land uses and/or prominent features that occur within +/- 500m radius of the site and neighbouring properties if these are located beyond 500m of the site.
Please note: The Department may request specialist input/studies depending on the nature of the land use character of the area and potential impact(s) of the proposed activity/ies.
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Untransformed area Low density residential Medium density residential
High density residential Informal residential
Retail Commercial & warehousing (brickworks)
Light industrial (brickworks) Medium industrial Heavy industrial
Power station Office/consulting room Military or police base/station/compound
Casino/entertainment complex
Tourism & Hospitality facility
Open cast mine Underground mine Spoil heap or slimes dam
Quarry, sand or borrow pit (Transand)
Dam or reservoir (small dams)
Hospital/medical center School/Crèche Tertiary education
facility Church Old age home
Sewage treatment plant
Train station or shunting yard Railway line Major road (4 lanes or
more) Airport
Harbour Sport facilities Golf course Polo fields Filling station
Landfill or waste treatment site Plantation Agriculture River, stream or
wetland Nature conservation area/Conservancy
Mountain, koppie or ridge Museum Historical building Graveyard Archeological site
Other land uses (describe):
(b) Please provide a description, including the distance and direction to the nearest residential area and industrial area. The image below shows the typical land use of the surrounding area as described in the table above.
Figure 32: The figure illustrates the land uses surrounding the development site.
9. SOCIO-ECONOMIC ASPECTS
Describe the existing social and economic characteristics of the community in order to provide baseline information. Socio-Economic Context of the Mossel Bay Municipal Area.
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According to the Mossel Bay IDP (2012), Mossel Bay has the 2nd largest population in the Eden
District with a population size of 117 840 in 2007 compared to 71 499 in 2001. The population grew
on average by 8.7 per cent between 2001 and 2007 as compared to the district wide growth of 2 %.
The IDP concludes that a population growth of this proportion is likely to place strain on existing
backlogs and the municipality‟s ability to effectively service the community. Mossel Bay‟s population
composition is as follows:
- children at 25.6%;
- economically active population at 67.3%; and
- persons aged 65 and older at 7.2%
The current gender ration is 111.6 males per 100 females. Overall there has been a shift in the
gender distribution in Mossel Bay. In 2001, there were 49.7% males to 50.3%females. In 2007, this
shifted to 52.8% males to 47.2 %females creating a shift in the female dominance in 2001 to a male
dominance from 2007. Mossel Bay‟s population distribution by race is as follows:
African racial group 41.6%
Coloured racial 37.9%
White racial group 19.2%
Representation by the Indian/Asian population in Mossel Bay is relatively small compared to
the other population groups.
The biggest employment contributors in the Mossel Bay Municipal are:
Construction 9%
Wholesale & retail 8%
Community: social & personal services 7%
Manufacturing 6%
The three largest economic sectors are:
Manufacturing (28.7%)
Finance & business services (27.5%)
Trade (13.4%)
The unemployment rate for males was 15.6% with a 44.5 percentage share of the unemployed. The
unemployment rate for females was significantly higher at 28.9% but the percentage share of the
unemployed lower at 55.5 %.
The 2012 IDP Housing statistics for the Mossel Bay Municipality are as follows:
Household infrastructure
Formal 21 484
Informal 4 181
Traditional 1 059
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Other dwelling types 62
Total 26 786
The formal dwelling backlog (number of households not living in a formal dwelling) was recorded as
5 302 in 2009.
Sanitation (recorded in 2009)
Flush toilet 25 621
Ventilation improved pit 52
Pit toilet 359
Bucket system 146
No toilet 607
Total 26 786
The sanitation backlog recorded in 2009 was 1 112.
Access to water
Piped water inside dwelling 18,466 Piped water in yard 7,008 Communal piped water: less than 200m from dwelling 381 Communal piped water: more than 200m from dwelling 482 No formal piped water 449 Total 26,786
The water backlog (number of households below RDP level) for 2009 was 931.
The number of households with no electrical connection estimated at 3 315 in 2009.
The number of households with no refuse removal in 2009 was 1,390
Please note that this section deals with the socio economic context of the municipal area, the specific
socio economic context of the proposed development is dealt with in section D of this report.
10. HISTORICAL AND CULTURAL ASPECTS
(a) Please be advised that if section 38 of the National Heritage Resources Act, 1999 (Act No. 25 of 1999), is applicable to
your proposed development, then you are requested to furnish this Department with written comment from Heritage
Western Cape as part of your public participation process. Section 38 of the Act states as follows: “38. (1) Subject to the
provisions of subsections (7), (8) and (9), any person who intends to undertake a development categorised as-
(a) the construction of a road, wall, power line, pipeline, canal or other similar form of linear development or barrier exceeding 300m in length;
(b) the construction of a bridge or similar structure exceeding 50m in length; I any development or other activity which will change the character of a site- (i) exceeding 5 000 m2 in extent; or (ii) involving three or more existing erven or subdivisions thereof; or (iii) involving three or more erven or divisions thereof which have been consolidated within the past five years; or (iv) the costs of which will exceed a sum set in terms of regulations by SAHRA or a provincial heritage resources
authority; (d) the re-zoning of a site exceeding 10 000 m2 in extent; or (e) any other category of development provided for in regulations by SAHRA or a provincial heritage resources
authority,
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must at the very earliest stages of initiating such a development, notify the responsible heritage resources authority and furnish it with details regarding the location, nature and extent of the proposed development.‖
(b) The impact on any national estate referred to in section 3(2), excluding the national estate contemplated in section
3(2)(i)(vi) and (vii), of the National Heritage Resources Act, 1999 (Act No. 25 of 1999), must also be investigated, assessed
and evaluated. Section 3(2) states as follows: “3(2) Without limiting the generality of subsection (1), the national estate may
include—
(a) places, buildings, structures and equipment of cultural significance; (b) places to which oral traditions are attached or which are associated with living heritage; I historical settlements and townscapes; (d) landscapes and natural features of cultural significance;
(e) geological sites of scientific or cultural importance; (f) archaeological and palaeontological sites; (g) graves and burial grounds, including— (i) ancestral graves; (ii) royal graves and graves of traditional leaders; (iii) graves of victims of conflict; (iv) graves of individuals designated by the Minister by notice in the Gazette; (v) historical graves and cemeteries; and (vi) other human remains which are not covered in terms of the Human Tissue Act, 1983 (Act No. 65 of 1983); (h) sites of significance relating to the history of slavery in South Africa; (i) movable objects, including— (i) objects recovered from the soil or waters of South Africa, including archaeological and palaeontological objects and material, meteorites and rare geological specimens; (ii) objects to which oral traditions are attached or which are associated with living heritage; (iii) ethnographic art and objects; (iv) military objects; (v) objects of decorative or fine art; (vi) objects of scientific or technological interest; and (vii) books, records, documents, photographic positives and negatives, graphic, film or video material or sound recordings, excluding those that are public records as defined in section 1(xiv) of the National Archives of South Africa Act, 1996 (Act No. 43 of 1996).‖
Is section 38 of the National Heritage Resources Act, 1999, applicable to the development? YES NO
UNCERTAIN
If YES, explain:
The following activities are applicable to the proposed development.
(a) the construction of a road, wall, power line, pipeline, canal or other similar form of
linear development or barrier exceeding 300m in length;
(c) any development or other activity which will change the character of a site-
(i) exceeding 5 000 m2 in extent; or
(ii) involving three or more existing erven or subdivisions thereof; or
(d) the re-zoning of a site exceeding 10 000 m2 in extent;
A Heritage assessment and Notice of Intent to Develop (NID, Annexure G5) was
submitted to Heritage Western Cape (HWC) by De Kock (2014) who recommended
that an Archaeological Impact Assessment (AIA) be conducted due to the sensitive
archaeological nature of coastal areas in the Mossel Bay district. Preliminary
comment from HWC confirmed the need for an AIA. The AIA can be viewed in
Annexure G1.
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Will the development impact on any national estate referred to in section 3(2) of the National Heritage
Resources Act, 1999?
YES NO
UNCERTAIN
If YES, explain:
Will any building or structure older than 60 years be affected in any way? YES NO UNCERTAIN
If YES, explain:
Please Note: If uncertain, the Department may request that specialist input be provided.
11. APPLICABLE LEGISLATION, POLICIES AND/OR GUIDELINES
(a) Please list all legislation, policies and/or guidelines that have been considered in the preparation of this Basic Assessment Report.
LEGISLATION ADMINISTERING
AUTHORITY
TYPE Permit/ license/
authorisation/comment / relevant consideration (e.g.
rezoning or consent use,
building plan approval)
DATE (if already obtained):
National Environmental
Management Act
Department of
Environmental Affairs
Basic Assessment
process
Act 107 of 1998 as
amended
National Environmental
Management:
Biodiversity Act
Department of
Environmental Affairs
CapeNature
Basic Assessment
process
Act 10 of 2004
National Water Act Department of Water
Affairs
Water Use Licence
Application (WULA)2
Awaiting response
from DWA
National Spatial
Biodiversity
Assessment
CapeNature CBA and ESA areas 2011
Garden Route
Biodiversity Sector
Plan
CapeNature CBA and ESA areas
Conservation of
Agricultural Resources
Act
Department of
Agriculture, Forestry &
Fisheries
Clearing of alien
vegetation as listed ito
CARA
Act 43 of 1983
2 The closest point of the proposed activity is ±260m from the Hartenbos River, however ±60% of the proposed development will be further than 500m from the Hartenbos River. Between the proposed development and the Hartenbos River there is a road (R328), residential and farming buildings, agricultural lands, and Transand Brickworks. Although within 500m from a river/wetland, the proposed development will not (as stated in Section 21(c) & (i) of the NWA) impede, or divert the flow of the watercourse; alter the bed, banks, course or characteristics of this watercourse. It is therefore the opinion of this office that a WULA is not required
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National Veld and
Forest Fire Act
Department of
Agriculture, Forestry &
Fisheries
Proximity to forestry
areas.
Act 101 of 1998
Nature & Environment
Conservation
Ordinance
CapeNature Endangered vegetation
type as well as CBA
and ESA.
Ordinance 19 of 1974
National Heritage
Resources Act
Heritage Western
Cape
Activity greater than
5000m2.
Act 25 of 1999
Land Use Planning
Ordinance
Mossel Bay
Municipality
Rezoning application Ordinance 15 of 1985
POLICY/ GUIDELINES ADMINISTERING AUTHORITY
National Building Regulations Building Inspectors from the local Authority
(Mossel Bay Municipality)
SANS 10400 (National Building Standards) Building Inspectors from the local Authority
(Mossel Bay Municipality)
The Red Book, SABS 1200LE, COLTO 2000,
SANRAL Drainage Manual
Implementation of the Environmental
Authorisation
Spatial Development Framework (2013) Mossel Bay Municipality
Community Safety By-Law Mossel Bay Municipality
DEA&DP EIA Guideline Information Document
on Generic Terms of Reference for EAPs and
Project Schedules (August 2010)
DEA&DP
DEA&DP EIA Guideline on Need & Desirability
(August 2010)
DEA&DP
DEA&DP EIA Guideline on Alternatives (August
2010)
DEA&DP
DEA&DP Guidelines on Environmental
Management Plans (August 2010)
DEA&DP
DEA&DP Guideline for Determining the Scope of
Specialist Involvement (June 2005) DEA&DP
DEA&DP Guideline for Involving Biodiversity
Specialists in EIA processes (June 2005) DEA&DP
DEA&DP Guideline for Involving Heritage
Specialists (June 2005) DEA&DP
DEA&DP Guideline for Involving Visual &
Aesthetic Specialists in EIA processes (June
2005)
DEA&DP
(b) Please describe how the legislation, policies and/or guidelines were taken into account in the preparation of this Basic
Assessment Report.
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LEGISLATION / POLICY / GUIDELINE DESCRIBE HOW THE LEGISLATION / POLICY / GUIDELINE WERE TAKEN
INTO ACCOUNT (E.g. describe the extent to which it was adhered to, or deviated from, etc).
Spatial Development Framework (2013)
The Spatial Development Framework was consulted to determine whether the development proposal is in line with the framework‟s recommendations for land use.
DEA&DP EIA Guideline Information Document on Generic Terms of Reference for EAPs and Project Schedules (August 2010)
The EIA Guideline Information Document ToR for EAPs and Project Schedules were consulted to ensure that the EAP‟s conduction of the process and the Project Schedule of this application correspond to these requirements.
DEA&DP EIA Guideline on Need & Desirability (August 2010)
The EIA Guideline on Need & Desirability was consulted as part of the project motivation and section of this report describing the proposal‟s need & desirability.
DEA&DP Guidelines on Environmental Management Plans (August 2010)
The Environmental Management Plans Guidelines were consulted as part of the compiling of the Environmental Management Plan (EMP) for this application to ensure that the EMP prescribed complies with the Guidelines.
DEA&DP Guideline for Determining the Scope of Specialist Involvement (June 2005)
This Guideline was consulted and considered with initial site visit to determine the specialists necessary to inform the assessment of this application and development site.
DEA&DP Guideline for Involving Biodiversity Specialists in EIA processes (June 2005)
This Guideline was consulted and considered with initial site visit. It was determined that a Botanical specialist must be appointed to assess the impact of the proposed development on botanical resources.
DEA&DP Guideline for Involving Heritage Specialists (June 2005)
This Guideline was consulted and considered with initial site visit. The National Heritage Resources Act was also consulted and it was determined that a Heritage Specialist be appointed to assess the impact of the proposed development on any heritage resources.
DEA&DP Guideline for Involving Visual & Aesthetic Specialists in EIA processes (June 2005)
This Guideline was consulted and considered with initial site visit and given the urban nature of the immediate area, it is not necessary for a visual specialist to be involved.
Please note: Copies of any permit(s) or licences received from any other organ of state must be attached this report as Appendix E.
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SECTION C: PUBLIC PARTICIPATION The public participation process must fulfil the requirements outlined in NEMA, the EIA Regulations, and if applicable the NEM:
WA and/or the NEM: AQA. This Department‟s Guideline on Public Participation (August 2010) and Guideline on Exemption
Applications (August 2010), both of which are available on the Department‟s website (http://www.capegateway.gov.za/eadp),
must also be taken into account.
Please highlight the appropriate box to indicate whether the specific requirement was undertaken or whether there was a deviation that was agreed to by the Department.
1. Were all potential interested and affected parties notified of the application by –
(a) fixing a notice board at a place conspicuous to the public at the boundary or on the fence of - (i) the site where the activity to which the application relates is to be undertaken; and
YES DEVIATED
(ii) any alternative site mentioned in the application; YES DEVIATED
(b) giving written notice to –
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(i) the owner or person in control of that land if the applicant is not the owner or person in control
of the land;
Notice was given to ATKV who is the owner of Erf 3122 and Portion 4 of
the Farm Hartenbosch 217. Written permission to conduct the environmental process and develop
low cost housing opportunities on the land was granted by the ATKV in
writing – Annexure E1.
YES N/A
(ii) the occupiers of the site where the activity is to be undertaken and to any alternative site where
the activity is to be undertaken; YES DEVIATED
(iii) owners and occupiers of land adjacent to the site where the activity is to be undertaken and to
any alternative site where the activity is to be undertaken; YES DEVIATED
(iv) the municipal councillor of the ward in which the site and alternative site is situated and any organisation of ratepayers that represent the community in the area;
YES DEVIATED
(v) the municipality which has jurisdiction in the area; YES DEVIATED
(vi) any organ of state having jurisdiction in respect of any aspect of the activity; and YES DEVIATED
(vii) any other party as required by the competent authority; YES DEVIATED
I placing an advertisement in -
(i) one* local newspaper; and YES DEVIATED
(ii) any official Gazette that is published specifically for the purpose of providing public notice of applications or other submissions made in terms of these Regulations;
YES DEVIATED N/A
(d) placing an advertisement in at least one* provincial newspaper or national newspaper, if the activity has or may have an impact that extends beyond the boundaries of the metropolitan or local municipality in which it is or will be undertaken.
YES DEVIATED N/A
* Please note: In terms of the NEM: WA and NEM: AQA a notice must be placed in at least two newspapers circulating in the
area in which the activity applied for is to be carried out.
2. Provide a list of all the state departments that were consulted:
Department of Human Settlements Charl Louw
Department of Agriculture, Forestry and Fisheries Cobri Vermeulen
Department of Agriculture Cor vd Walt
Department of Health: Province Manie Abrahams
Department of Water Affairs Caroline Tlowana & Hester Lyons
Heritage Western Cape Calvin van Wijk
Eden District Municipality Vernon Gibbs
CapeNature Clyde Lamberts/Benjamin Walton
Mossel Bay Municipality: Housing Johan van Zyl
Mossel Bay Municipality: Planning Carel Venter, Eddie Kruger & Dries Cilliers
Mossel Bay Municipality: Technical Services Eric Louw
Mossel Bay Municipality: Electrical Dick Naidoo
Mossel Bay Municipality: Health Lanese Hesselman
Mossel Bay Municipality: Environmental Warren Manuel
Ward 7 Councillor Jim van der Merwe
Provincial Roads Cornelius Malgas & Malcolm Watters
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3. Please provide an overall summary of the Public Participation Process that was followed. (The detailed outcomes of this process must
be included in a comments and response report to be attached to the final Basic Assessment Report (see note below) as Appendix F).
The general public was informed of the process and invited to register as an Interested & Affected
Party (I&AP) through a newspaper advert that appeared in the Mossel Bay Advertiser on 13
June 2014. This advert was placed in English calling for I&APs to submit their contact details and
any preliminary comments they may have to Cape EAPrac. Specific information was given about
deviations and exemption being applied for as part of this notice. I&APs were given 21-days to
register for the environmental process
Site notices were placed at the site in English, informing of the project proposal, deviations and
exemption, as well as how to register as an I&AP.
On 13 June 2014, neighbouring landowners were notified in writing of the proposed project and
environmental process. They were informed of their right to participate in the process and
requested to register as an I&AP should they have any issues/concerns regarding the proposed
development.
Direct neighbours in the existing Sonskynvallei township was notified on 13 June 2014 via letter-
drop, as the Mossel Bay Municipality was listed as the landowner in windeed. Letters was received
by either the landowner or family members who were at home at the time.
On 20 June 2014 a meeting took place in Councillor J. Van der Merwe‟s office in the Mossel Bay
Municipality‟s main building, Mossel Bay (see Annexure F3 for minutes and attendance register).
The following persons attended the meeting: Councillor J. Van der Merwe (Ward 7), Johan van Zyl
(Mossel Bay Municipality: Housing Manager), Warren Manuel (Mossel Bay Municipality:
Environment), Delarey Viljoen (DELplan), Louise-Mari van Zyl (Cape EAPrac: Director) and
Wynand Loftus (Cape EAPrac). It was established that a meeting with the ward committee can be
arranged through Councillor Van der Merwe. The meeting was scheduled for 2 July 2014 at the
Sonskynvallei community hall. Other points of discussion included, but are not limited to:
Visual Impact Assessment will be required.
A Background Information Document will be complied by Cape EAPrac and distributed to
the Agricultural Society (and other interested parties) via the Councillor.
Environmental Education for erosion and the possibility of a tree planting programme post
construction was suggested.
Community currently complain about strong water flow during rains. Stormwater
management is essential (included in the civil services report).
In terms of layout, explore the possibility of duplex units for the proposed development in
order to minimise visual impact.
On 2 July 2014 a meeting took place at the Sonskynvallei Community Centre to discuss the
proposed project with the ward committees of Sonskynvallei and Hartenbosheuwels. Councillor J.
Van der Merwe, DELplan, Cape EAPrac and representatives of the Mossel Bay Municipality
(Planning and Environment) was also present. Ward committee members was given a
Background Information Document containing information regarding the proposed development
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and the Environmental Process was explained. Cape EAPrac gave an overview of the process up
to date and attendees were given ample opportunity to ask questions.
In the above mentioned meeting the community enquired about the possibility of keeping the
Gumpiro Street access point, instead of closing it and only using Mandela Road as a single
access point to the neighbourhood as recommended by the Traffic Impact Assessment. The TIA
recommends the Gumpiro access point be closed due to safety regulations. The community
suggested that the sight distance of the access point can be increase, thus increasing the safety, if
the vegetation in the road reserve be cleared. The engineer who compiled the TIA (Henry Maart)
was asked to respond to the community‟s request and explain why the Gumpiro Street access
point must be closed, his response was as follows:
- The TIA takes into account the published guidelines of the Western Cape Government,
who is the roads authority on TR33/2.
- The guidelines are based on safety, proper sight distances, reaction times and roadside
markings, etc.
- The existing access points in question are substandard in terms of access spacing.
- Moving it more to the EAST will increase the vertical separation between the two roads
that must be joined. This will create a steep access into the suburb and also bring about
lower shoulder sight distance values towards the West. This will create a substandard
second access while we are of the opinion that the Mandela junction is sufficient.
14 July 2014. Distribute BID to registered I&APs, relevant state departments and authorities.
16 July 2014. The Western Cape Government Department of Health made the following
comment: “The Department has no objection to the proposed development, subject to the
following conditions:
- Mossel Bay Municipality must supply all drinking water;
- Sewage must be connected to the Municipal sewage system; and
- All refuse waste must be removed by the Mossel Bay Municipality.”
Letter dated 27 August 2014 was received from the Department of Agriculture who requested
that the impact on agriculture be indicated. Further correspondence with the Department resulted
in the Department revising its comment, stating that a study indicating the impact on agriculture is
not required (email received 13 October 2014).
5 September 2014. Receive initial comment on the project from Billy Robertson. Points raised
include: Erf boundaries, neighbouring properties, flood plain, natural Renosterveld & safety of
pedestrians (Annexure F4). Mr Robertson‟s comments were responded, refer to Comments and
Responses Table (Annexure F8)
29 September 2014. Post Notification letters of the availability of the DBAR to I&APs who has no
email address. Courier CD copies to commenting state departments (Annexure F5).
30 September 2014. Email Notification letter of the availability of the DBAR to registered I&APs.
1 October 2014. Draft BAR made available to public and registered I&APs for 40-day commenting
period. A hard copy of the DBAR was placed at the Mossel Bay Municipality‟s Planning
Department, Hartenbos Library and the Sonskynvallei Clinic. Registered I&APs was also informed
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of a digital copy of the DBAR available on the Cape EAPrac website.
All registered I&APs were notified of the availability of the DBAR, see Annexure F5 – Draft BAR
Notifications.
9 October 2014. Mr Faan Gerber from the Hartenbosheuwels Home Owners Association
commented on the DBAR saying that they have no issues with the proposed development. Mr
Gerber enquired about the development plan and whether it makes provision for a school. He
believes there no need for a new school as there is already one. The Hartenbos Care Centre is
the governing body of the existing body and will have to be informed if/when school expansion
was to take place. Mr Gerber‟s comments and responses thereto can be seen in the Comments
and Responses Table (Annexure F8).
On 15 October 2014 this office received the following comment from the Department Transport
and Public works:
This branch will not be opposed to the issuing of an Environmental Authorisation, provided that a
Land Use Planning Ordinance (LUPO) application is submitted via the Local Authority to this
Branch.
At this stage this Branch can state the following:
- It accepts the motivation of the Traffic Impact Study
- The following accesses will have to be closed:
- Off Trunk Road 33 section 2 at ±km0.88 LHS (waste disposal)
- Off Trunk Road 33 section 2 at ±km0.94 LHS (Gumpiro Avenue)
- Mandela Street off Trunk Road 33 section 2 at ±km0.94 LHS will have to be upgraded as per
SMEC‟s recommendation (Traffic Impact Assessment).
The proposed layout must be amended in order to be able to construct another access, when
required, onto Trunk Road 33 section 2 at ±km1.78 LHS (opposite the mine). This comment was
discussed with the planners and reflected in the latest proposed development layout (Appendix B
– plan dated November 2014)
On 28 October 2014 the Department of Health George Office stated that it has no further
comment regarding the proposed development. The department confirmed that it be removed from
the I&AP register (Annexure F6).
On 10 November 2014 this office received a letter from the Department of Water Affairs (DWA),
commenting on the proposed development. The DWA has no objection to the proposed
development on subject to all relevant sections and regulations of the National Water Act,
regarding water use and the conditions listed below (please refer to Annexure F6 to view the full
comment of the DWA):
- Letter in which Mossel Bay Municipality confirms the availability of potable water and sewage
treatment capacity must be submitted to the DWA;
- Storm water management infrastructure must be to the satisfaction of the Mossel Bay Municipality;
- No activity may take place within 1:100 year flood line, riparian areas or within 500m from a
wetland; and
- Surface and/or groundwater pollution must be dealt with in accordance with Section 19 & 20 of the
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National Water Act.
Please note:
Should any of the responses be “No” and no deviation or exemption from that requirement was requested and
agreed to /granted by the Department, the Basic Assessment Report will be rejected.
A list of all the potential interested and affected parties, including the organs of State, notified and a list of all the
register of interested and affected parties, must be submitted with the final Basic Assessment Report. The list of
registered interested and affected parties must be opened, maintained and made available to any person
requesting access to the register in writing.
The draft Basic Assessment Report must be submitted to the Department before it is made available to interested
and affected parties, including the relevant organs of State and State departments which have jurisdiction with
regard to any aspect of the activity, for a 40-day commenting period. With regard to State departments, the 40-
day period commences the day after the date on which the Department as the competent/licensing authority
requests such State department in writing to submit comment. The applicant/EAP is therefore required to inform
this Department in writing when the draft Basic Assessment Report will be made available to the relevant State
departments for comment. Upon receipt of the Draft Basic Assessment Report and this confirmation, this
Department will in accordance with Section 24O(2) and (3) of the NEMA request the relevant State departments
to comment on the draft report within 40 days.
All comments of interested and affected parties on the draft Basic Assessment Report must be recorded,
responded to and included in the Comments and Responses Report included as Appendix F to the final Basic
Assessment Report. If necessary, any amendments in response to comments received must be effected in the
Basic Assessment Report itself. The Comments and Responses Report must also include a description of the
public participation process followed.
The final Basic Assessment Report must be made available to registered interested and affected parties for
comment before submitting it to the Department for consideration. Unless otherwise indicated by the Department,
a final Basic Assessment Report must be made available to the registered interested and affected parties for
comment for a minimum of 21-days. Comments on the final Basic Assessment Report does not have to be
responded to, but the comments must be attached to the final Basic Assessment Report.
The minutes of any meetings held by the EAP with interested and affected parties and other role players which
record the views of the participants must also be submitted as part of the public participation information to be
attached to the final Basic Assessment Report as Appendix F.
Proof of all the notices given as indicated, as well as of notice to the interested and affected parties of the
availability of the draft Basic Assessment Report and final Basic Assessment Report must be submitted as part of
the public participation information to be attached to the final Basic Assessment Report as Appendix F.
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SECTION D: NEED AND DESIRABILITY Please Note: Before completing this section, first consult this Department‟s Guideline on Need and Desirability (August 2010) available on the Department‟s website (http://www.capegateway.gov.za/eadp).
1. Is the activity permitted in terms of the property‟s existing land use rights? YES NO Please explain
The development site is currently zoned as Agriculture I and Authority Zone. The land will be re-zoned
for the proposed housing development. The site is however indicated in all relevant spatial tools as
being suitable for township development as it falls within the urban edge. 2. Will the activity be in line with the following?
(a) Provincial Spatial Development Framework (PSDF) YES NO Please explain
The PSDF promotes infill development and proximity to existing services. The PSDF further promotes
the provision of affordable housing to address the housing backlog within Municipal areas. (b) Urban edge / Edge of Built environment for the area YES NO Please explain
The development site falls within the urban edge for this area. (c) Integrated Development Plan and Spatial Development Framework of the Local
Municipality (e.g. would the approval of this application compromise the integrity of the
existing approved and credible municipal IDP and SDF?).
YES NO Please explain
The IDP promotes the planning and supply of affordable housing to local communities.
The property falls within the area designated for township expansion. (d) Approved Structure Plan of the Municipality YES NO Please explain
(e) An Environmental Management Framework (EMF) adopted by the Department
(e.g. Would the approval of this application compromise the integrity of the existing
environmental management priorities for the area and if so, can it be justified in terms of
sustainability considerations?)
YES NO Please explain
No adopted EMF available for this area. (f) Any other Plans (e.g. Guide Plan) YES NO Please explain
3. Is the land use (associated with the activity being applied for) considered within the timeframe intended by the existing approved Spatial Development Framework (SDF) agreed to by the relevant environmental authority (i.e. is the proposed development in line with the projects and programmes identified as priorities within the credible IDP)?
YES NO Please
explain
The proposed development is recognised in the SDF and IDP. 4. Should development, or if applicable, expansion of the town/area concerned in terms
of this land use (associated with the activity being applied for) occur here at this point in time?
YES NO Please
explain
The Mossel Bay Municipality has a responsibility to provide housing to its communities. The proposed
development will address the housing need of the area and falls within the urban edge of Mossel Bay. 5. Does the community/area need the activity and the associated land use concerned (is
it a societal priority)? (This refers to the strategic as well as local level (e.g. development is a national priority, but within a specific local context it could be inappropriate.)
YES NO Please
explain
The PSDF promotes the provisioning of affordable housing to address the housing backlog within
Municipal areas. The local community, by means of their Councillor & Ward Committee have indicated
their support for the housing project as there is a considerable housing need in the Mossel Bay area.
6. Are the necessary services with adequate capacity currently available (at the time of application), or must additional capacity be created to cater for the development?
YES NO Please
explain
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(Confirmation by the relevant Municipality in this regard must be attached to the final Basic Assessment Report as Appendix E.)
The proposed development will have to install water, sewage and electricity to the individual Erven. The
Civil Services report (Annexure G3) has indicated that upgrades at the Hartenboskop reservoir will be
required for bulk water supply and a new bulk water pipeline will have to be installed. It was confirmed
by GLS Consulting that an additional 1200kl reservoir storage is required at the existing 3500kl
Hartenboskop reservoir. The storage in the new reservoir will be shared by the proposed Sonskynvallei
development and other proposed developments in the supply area of the new reservoir. In addition to
the increase of the Hartenboskop reservoir storage capacity, a bulk water supply line will be required
from the reservoir to the proposed site.
A 1415m x 200mm pipeline following in part the route of an existing 100mm diameter bulk line servicing
the Brandwag township is proposed. A portion of the pipeline will be aligned alongside the above
mentioned 100mm pipeline within a registered servitude, the remainder of the pipeline will follow an
existing track leading to the Hartenboskop reservoir. The recommended alignment is illustrated in Figure
4.
Additional sewage flow generated by the proposed housing development can be accommodated by the
existing waste water treatment works (Du Preez, 2014).
New sewer line with rising main will be installed and connected to the existing Sonskynvallei
pumpstation which has sufficient capacity to accommodate the additional flow.
Electricity supply will be provided from the newly built 66/11kV 20MVA Substation situated
approximately 1km east of the proposed development (CVW Electrical 2014; Annexure E2).
7. Is this development provided for in the infrastructure planning of the municipality, and if not what will the implication be on the infrastructure planning of the municipality (priority and placement of services and opportunity costs)? (Comment by the relevant Municipality in this regard must be attached to the final Basic Assessment Report as Appendix E.)
YES NO Please
explain
The proposed bulk water upgrades (Annexure G3) will ensure that the municipality has sufficient
infrastructure to service the proposed development.
8. Is this project part of a national programme to address an issue of national concern or importance?
YES NO Please
explain
Meeting the basic needs of local communities through the provisioning of basic services and housing
opportunities is seen as an issue of national concern. 9. Do location factors favour this land use (associated with the activity applied for) at this
place? (This relates to the contextualisation of the proposed land use on this site within its broader context.)
YES NO Please
explain
The proposed Phase 3 Sonskynvallei housing development form part of a greater housing development
i.e. Phases 1 & 2. The location of the proposed development is adjacent to the before mentioned phases
and thus in line with the Municipality‟s long term strategy for the area.
10. How will the activity or the land use associated with the activity applied for, impact on sensitive natural and cultural areas (built and rural/natural environment)?
YES NO Please
explain
A heritage Specialist Assessment was undertaken by Stefan de Kock of PERCEPTION Planning for the
proposed development (De Kock, 2014; Annexure G5). It was indicated by De Kock (2014) that no
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historic structures, ruins or gravesites were found during field work. The heritage report also stated that
no significant structures and/or cultural landscape patterns could be identified through early aerial
imagery.
Due to the general sensitive archaeological nature of coastal areas in the Mossel Bay area, the heritage
specialist recommended that an archaeological impact assessment be undertaken for this area. The
specialist also recommended that archaeological monitoring may be required during future earthworks
and excavations associated with the proposal, which would include installation of the proposed bulk
water pipeline.
An Archaeological Impact Assessment (AIA) conducted by Nilssen (2014) found no objections to the
proposed development in terms of archaeology (i.e. no significant archaeoligical resources will be
impacted by the proposed development) and recommended that no further work is needed in this regard
(Annexure G1).
11. How will the development impact on people‟s health and wellbeing (e.g. in terms of noise, odours, visual character and sense of place, etc)?
YES NO Please explain
The installation of basic services (potable water, sewerage, stormwater management, roads and waste
removal services) will have a positive impact on the health of the people that are to be relocated to the
site, as well as the environmental health of the site and surrounding natural systems.
The visual character will be impacted by transforming a vacant area to a built environment, however
within the context of the urban edge and adjacent built environment (housing and industrial) this change
in visual character is unlikely to have a negative impact on people’s health and wellbeing. The Visual
Impact Statement (Annexure G7) by Stephen Stead from Visual Resource Management Africa cc state
that the proposed development (preferred alternative) does not constitute a significant visual impact.
In terms of sense of place, the prosed development will provide much needed housing which will
establish ownership and a sense of place within the new community.
12. Will the proposed activity or the land use associated with the activity applied for, result in unacceptable opportunity costs?
YES NO Please
explain
The proposed development forms part of the strategic long-term housing strategy of the Mossel Bay
Municipality.
13. What will the cumulative impacts (positive and negative) of the proposed land use associated with the activity applied for, be?
YES NO Please
explain
Potential cumulative impacts include the following:
Provide high density housing opportunities (positive, long term) in an area with housing
shortages;
Potential pollution from construction activities and activities of residents (negative, short term,
can be mitigated);
Potential erosion as a result of construction activities (negative, short term, can be mitigated);
Waste, sewage and stormwater services to housing beneficiaries (positive, long term); and
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(17) Please describe how the general objectives of Integrated Environmental Management as set out in section 23 of NEMA have been taken into account: The purpose of Section 23 of NEMA is to promote the application of appropriate environmental
management tools in order to ensure the integrated environmental management of activities. The aim
of these principles is to identify, predict and evaluate the actual and potential impact on the
environment (including socio-economic and cultural environments), to assess alternatives and
propose mitigation options which will contribute to minimizing detrimental impact.
For this application, actual and potential impacts on the various environments have been considered
and assessed. The following specialist input was considered during the completing of this Basic
Assessment:
Archaeological
Botanical
Civil
Electrical
Heritage
Planning
Traffic
Visual
The nature of the application results in minimal impacts, with positive impacts for beneficiaries who will
be residing in the proposed development. The proposed development has been planned in a way to
avoid the intact patch of thicket on the western side of the development patch as well as semi-intact
Impact of subsidised housing on operations and values of surrounding businesses (negative, long term).
It is believed that the manner in which the proposed Sonskynvallei Housing Extension Phase 3
development is planned, answers to the challenges of need and desirability taking into account that the
area is (has been) designated for township development in municipal spatial planning tools. The land
use is not considered to be in conflict with other existing land uses in the area.
14. Is the development the best practicable environmental option for this land/site? YES NO Please
explain
The development is in-line with the strategic long-term housing strategy of the Mossel Bay Municipality.
Formal services like stormwater management, sewage and waste removal will mitigate the potential
environmental impact of the development.
15. What will the benefits be to society in general and to the local communities? Please
explain
Positive. To provide much needed housing to the local community members in an area that has housing need.
16. Any other need and desirability considerations related to the proposed activity? Please
explain
All considerations have been covered above.
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thicket patches around the rugby field. The most valuable/conservation-worthy patch of thicket can
connect to thicket adjacent to the site and impacts on this vegetation must be managed and minimised
where possible. Potential pollution on surrounding areas is of high concern. Mitigation measures as
set out in the Environmental Management Programme (EMP) needs to be followed in order to
minimise the potential impacts on the surrounding natural environment.
The proposed infrastructure development, along with the generous Public Open Space areas will
mitigate the possibility of pollution through sewage, waste and stormwater (erosion).
Finally, in accordance with the Integrated Environmental Management principles, ample opportunity is
being allowed for public participation. An advert has been placed in the local newspaper, informing
members of the public of the proposal and available information, and included details on how
members of the public can register as stakeholders and through doing so, form part of the
environmental process. Other key stakeholders (e.g. Councillor, direct neighbours, CapeNature,
Mossel Bay Municipality) have been identified and notified of the process. A Notice Board was placed
at the development site. Initial comment received prior to the completion of the DBAR is included in
this report (Annexure F4). The public advertisement and notices sent to identified stakeholders,
included details on the Draft Basic Assessment Report’s availability and how comment can be
submitted on the application. Comments received on the Draft Basic Assessment Report were
considered by the project team, responded to, and is included in this Final Basic Assessment Report.
All registered I&APs were informed of the availability of the FBAR for comment and review period of
21 days. All comments received on the FBAR will be included in the FBAR that will be submitted to the
DEA&DP for decision making.
(18) Please describe how the principles of environmental management as set out in section 2 of NEMA have been taken into account: The main and applicable principles of environmental management as set out in Section 2 of NEMA
emphasises the following:
Environmental management placing people and their needs at forefront of its concern, and
serve their physical, physiological, developmental, cultural and social interests equitably – the
proposed development will not exceed beyond the building restriction area. Potential pollution
aspects have been addressed and can be mitigated successfully through implementation of
the EMP. I&APs and Stakeholders are allowed the opportunity to consider and submit
comment in terms of the proposal.
Socially, environmentally and economically sustainable development – the proposed
development forms part of the Mossel Bay Municipality’s long term housing strategy.
The cultural/heritage significance of the site has been assessed and the specialist reported
that no heritage resources will be affected by the proposed development.
The archaeological impact assessment (AIA) found that the proposed development will not
have a negative impact on any significant archaeological resources and indicated that no
further work with regard to archaeology is needed. Mitigation measures pertaining to the
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exposure of significant archaeological resources and human remains during construction are
laid out in the AIA.
Waste generated by the proposed development will be removed and managed through the
existing Municipal waste management system.
Landscape disturbance – The development site is adjacent to the existing Sonskynvallei
Township and is considered to be in-line with the surrounding land-use character.
Recommendations related to water and energy conservation have been included in the
Environmental Management Programme (EMP) for implementation.
Recommendations in terms of site demarcation and no-go areas, as well as service
installation and maintenance (e.g. a variety of retaining and stormwater control structures etc.)
have been made in line with a risk-averse and cautious approach.
The most viable, practical and environmentally-conservative options have been pursued
where possible.
Mitigation and monitoring measures have been recommended to minimise and avoid
potential contamination / degradation of the environment (through alien plant removal, anti-
erosion measures, etc).
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SECTION E: ALTERNATIVES Please Note: Before completing this section, first consult this Department‟s Guideline on Alternatives (August 2010) available on the Department‟s website (http://www.capegateway.gov.za/eadp). “Alternatives”, in relation to a proposed activity, means different means of meeting the general purposes and requirements of the activity, which may include alternatives to –
(a) the property on which, or location where, it is proposed to undertake the activity; (b) the type of activity to be undertaken; I the design or layout of the activity; (d) the technology to be used in the activity; (e) the operational aspects of the activity; and (f) the option of not implementing the activity.
The NEMA prescribes that the procedures for the investigation, assessment and communication of the potential consequences or impacts of activities on the environment must, inter alia, with respect to every application for environmental authorisation –
ensure that the general objectives of integrated environmental management laid down in NEMA and the National Environmental Management Principles set out in NEMA are taken into account; and
include an investigation of the potential consequences or impacts of the alternatives to the activity on the environment and assessment of the significance of those potential consequences or impacts, including the option of not implementing the activity.
The general objective of integrated environmental management is, inter alia, to “identify, predict and evaluate the actual and potential impact on the environment, socio-economic conditions and cultural heritage, the risks and consequences and alternatives and options for mitigation of activities, with a view to minimising negative impacts, maximising benefits, and promoting compliance with the principles of environmental management” set out in NEMA. 1. In the sections below, please provide a description of any identified and considered alternatives and alternatives that were
found to be feasible and reasonable. Please note: Detailed written proof the investigation of alternatives must be provided and motivation if no reasonable or feasible alternatives exist.
(a) Property and location/site alternatives to avoid negative impacts, mitigate unavoidable negative impacts and maximise
positive impacts, or detailed motivation if no reasonable or feasible alternatives exist: The property has been identified as a suitable site for the proposed development – this has been
confirmed through specialist reports.
High density residential developments appear in the SDF and the proposed development will be able
to gain access to services like sewage, waste and electricity by connecting to the existing system of
the Sonskynvallei township.
No alternative site(s) have been investigated.
(b) Activity alternatives to avoid negative impacts, mitigate unavoidable negative impacts and maximise positive impacts, or detailed motivation if no reasonable or feasible alternatives exist: The property has been identified as a suitable site for the proposed development – this has been confirmed through specialist reports.
High density residential developments appear in the SDF and the proposed development will be able
to gain access to services like sewage, waste and electricity by connection to the existing system of
the Sonskynvallei residential area.
The site falls within the urban edge of Mossel Bay adjacent to the existing Sonskynvallei Township.
No activity alternative has been considered.
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(c) Design or layout alternatives to avoid negative impacts, mitigate unavoidable negative impacts and maximise positive impacts, or detailed motivation if no reasonable or feasible alternatives exist:
Design alternatives: Free standing residential units (Alternative 1) and semi-detached units
(Alternative 2) are being considered.
Figure 33: 3D images of the proposed structures for the Sonskynvallei Phase 3 housing extension. Single free-standing units are illustrated in the back and semi-detached in the front (Stead, 2014).
Layout alternatives: Two Layout alternatives are being considered, the „initial layout‟
(Alternative 1) and „updated layout‟ (Alternative). The initial layout had limited input in terms of
specialists and consists of the single free-standing residential units. The updated layout
contains more specialist input, shows the semi-detached residential units (which reduce visual
intrusion as it results in less bulk) and is considered the preferred alternative. The alternative
layout can be seen in Appendix B, layout dated November 2014.
Realignment of the water pipeline for a section along the existing gravel track to avoid an
area identified as being sensitive.
(d) Technology alternatives (e.g. to reduce resource demand and resource use efficiency) to avoid negative impacts, mitigate unavoidable negative impacts and maximise positive impacts, or detailed motivation if no reasonable or feasible alternatives exist: SUDS (Sustainable Urban Drainage System) have been recommended by the Engineers to improve
overall stormwater management and reduce the potential for unwanted erosion i.e. swales (grassed
channels vs. hard surfaced open stormwater channels) and permeable surfaces rather than
impermeable surfaces where appropriate. (e) Operational alternatives to avoid negative impacts, mitigate unavoidable negative impacts and maximise positive impacts, or detailed motivation if no reasonable or feasible alternatives exist: No operational alternatives were considered. (f) the option of not implementing the activity (the No-Go Option): ALTERNATIVE 3
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The site is designated for township development in the relevant spatial planning tools for Mossel Bay
Municipality and is thus in line with the Municipality‟s housing strategy. There is a high level of
certainty that the site will be developed for housing purposes.
(g) Other alternatives to avoid negative impacts, mitigate unavoidable negative impacts and maximise positive impacts, or detailed motivation if no reasonable or feasible alternatives exist: No additional alternatives. (h) Please provide a summary of the alternatives investigated and the outcomes of such investigation: Please note: If no feasible and reasonable alternatives exist, the description and proof of the investigation of alternatives, together with motivation of why no feasible or reasonable alternatives exist, must be provided. The following alternatives are assessed as part of this application.
Alternative 1: Initial layout with free standing units
This alternative was informed through limited specialist input and contains the single free-standing
residential units. The Botanical Impact Statement indicated that there are areas of thicket close to the
rugby field that must be excluded from the development area. This was discussed with the planners
and is reflected in this alternative. See Appendix B, layout dated January 2014.
This alternative also allows for the water pipeline to be installed along the existing water servitude.
Alternative 2: Updated layout with semi-detached units (preferred)
Layout was informed through specialist assessments i.e. Visual and Botanical. This alternative takes
into account environmentally sensitive areas and contains the semi-detached dwellings which from a
Visual point of view will have less impact. This alternative further excludes sensitive/conservation-
worthy vegetation from the development layout as per recommendation from the specialist. It also
makes provision for a possible future access point opposite the mine, as recommended by the Dept.
Transport & Public Works. Alternative 2 is the preferred alternative. See Appendix B, layout dated
November 2014.
This alternative allows for a portion of the new water pipeline route to be realigned to follow the
existing gravel track to avoid an area identified as being sensitive (within the existing servitude).
Alternative 3: No-Go (Status quo)
No development.
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SECTION F: IMPACT ASSESSMENT, MANAGEMENT, MITIGATION AND MONITORING MEASURES
Please note: The information in this section must be duplicated for all the feasible and reasonable alternatives (where relevant).
1. DESCRIBE THE MANNER IN WHICH THE DEVELOPMENT WILL IMPACT ON THE FOLLOWING ASPECTS:
(a) Geographical and physical aspects: The site will be transformed from a natural environment to a built environment i.e. subsidy housing
opportunities.
The removal of vegetation and replacement with hard surfaces will increase the volume of runoff water
and subsequently increase the risk of erosion.
The engineers have however allowed for sufficient mitigation to address the potential impact
of erosion through providing for open grassed channels (swales), permeable surfacing
(where appropriate), water storage and re-use to reduce stormwater runoff volumes. Minor
storms (1:2 year) will be managed through a network of kerb inlets, grid inlets, open channels and below-ground pipes. Major storm events (1:50 year) will be managed through
overland flow via roads and footways, and attenuation storage within public open spaces
and within the road network, as appropriate. (b) Biological aspects: Will the development have an impact on critical biodiversity areas (CBAs) or ecological support areas (CSAs)? YES NO If yes, please describe:
Please read the explanations below in conjunction with the Critical Biodiversity Areas Map in Appendix
D of this report.
Terrestrial CBA
From the CBA data available for this area it appears that a small portion of the proposed bulk water
pipeline will cross a CBA at the existing reservoir.
The NFEPA broad scale mapping indicates a portion of the existing water pipeline servitude as being
sensitive. The latter area was also identified by the Botanical Specialist as being sensitive and was
subsequently excluded from the development area.
According to the Botanical specialist the most conservation worthy vegetation is around the rugby
field, particularly on its western side where thicket could possibly connect to thicket on the
neighbouring property (this area is picked up as an Aquatic CBA Buffer Area). As indicated by the
development layout, housing opportunities have been excluded from this area.
Aquatic CBA
With regards to Aquatic CBA‟s, the entire Portion 105 of Farm 217 (where the existing sports fields
are) is indicated as an Aquatic CBA buffer along with a section on the north-western boundary of the
development area (Appendix D). No Aquatic CBA‟s are indicated within the proposed development
area. It has to be noted that the existing Sonskynvallei township as well as neighbouring light industrial
areas are also indicated as Aquatic CBA buffers.
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The north-western Aquatic CBA buffer has been excluded from the development area due to the
sensitive nature of the vegetation (as per recommendation from the botanical specialist) and much of
the area surrounding the rugby field has been disturbed or transformed.
Will the development have on terrestrial vegetation, or aquatic ecosystems (wetlands, estuaries or the coastline)?
YES NO
If yes, please describe:
Terrestrial ecosystems The entire site is described as Groot Brak Dune Strandveld (Rebelo et al. 2006) and classified as
„Endangered‟ in terms of ecosystem status according to SANBI BGIS. On a finer scale the vegetation
of the development area is described as Herbertsdale Renoster Thicket and conforms better to this
description as Groot Brak Dune Strandveld is much too broad a description (Coetzee, 2014). The
proposed development will thus replace terrestrial vegetation. Sensitive and conservation worthy
vegetation have been excluded from the development footprint and a large section of the development
area to the south will be zoned Public Open Space. In the event that the sensitive vegetation,
excluded from the development area, can be managed (community project), i.e. kept clean of alien
plants and protected from vandalism and wood harvesting, the potential impact on the receiving
environment is likely to be HIGHLY POSITIVE.
Aquatic ecosystems
No areas indicated as National Freshwater Ecosystem Priority Areas (NFEPA) will be affected by the
footprint of the proposed development (Appendix D). However there are two areas within the larger
proposed development area indicated as NFEPA areas. The larger of the two areas is located within
an area which is proposed for Public Open Space (Appendix D) and will thus not be impacted directly
by the proposed development.
A very small section in the north-western part (where the true thicket occurs) is also indicated as an
NFEPA. By recommendation of the Botanical specialist this area has been excluded from the
development area and will also not be directly affected by the development.
Will the development have an impact on any populations of threatened plant or animal species, and/or on any habitat that may contain a unique signature of plant or animal species? YES NO
If yes, please describe:
According to SANBI BGIS the vegetation of the site, Groot Brak Dune Strandveld (on a finer scale
Herbertsdale Renoster Thicket) is classified as „Endangered‘ in terms of ecosystem status. The
Botanical Specialist has recommended that sensitive thicket areas along the north-western boundary
be excluded from the development area. Smaller thicket patches within the development site are
isolated and not conservation worthy.
The proposed development would thus not have a negative impact on threatened animal or plant
species, as these areas (conservation worthy) have been excluded from development area. The
Botanical Assessment suggested that the remainder of the proposed development site consisting
Grassy Renosterveld (mostly) is more suitable for the proposed housing development.
See Appendix D for vegetation map.
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Please describe the manner in which any other biological aspects will be impacted:
No other biological aspects will be impacted. (c) Socio-Economic aspects: What is the expected capital value of the activity on completion? Unknown What is the expected yearly income or contribution to the economy that will be generated by or as a result of the activity? Unknown
Will the activity contribute to service infrastructure? YES NO How many new employment opportunities will be created in the construction phase of the activity? Unknown What is the expected value of the employment opportunities during the construction phase? Unknown What percentage of this will accrue to previously disadvantaged individuals? Unknown How will this be ensured and monitored (please explain):
The Municipality, as the Applicant, will be responsible for implementing the project. As the local
Authority they are obliged to support a „local-first‟ policy through which preference should be given to
local contractors and job seekers. It is recommended that the appointed contractor make use of the
Municipality‟s list of job seekers and contractors to ensure maximum local employment. The
Contractor must keep record of employment records to ensure that the local community
(Sonskynvallei first, then neighbouring communities, then greater Mossel Bay area and then Garden
Route district for selection order) does benefit.
How many permanent new employment opportunities will be created during the operational phase of the activity? Unknown
What is the expected current value of the employment opportunities during the first 10 years? Unknown What percentage of this will accrue to previously disadvantaged individuals? Unknown How will this be ensured and monitored (please explain):
The Municipality, as the Applicant, will be responsible for implementing the project. As the local
Authority they are obliged to support a „local-first‟ policy through which preference should be given to
local contractors and job seekers. It is recommended that the appointed contractor make use of the
Municipality‟s list of job seekers and contractors to ensure maximum local employment. The
Contractor must keep record of employment records to ensure that the local community
(Sonskynvallei first, then neighbouring communities, then greater Mossel Bay area and then Garden
Route district for selection order) does benefit.
Any other information related to the manner in which the socio-economic aspects will be impacted:
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Housing demand pressure will be reduced in the Sonskynvallei area with beneficiaries who
are currently homeless, living in informal structures (i.e. backyard dwellers), or renting rooms
will be able to qualify for the housing scheme.
Existing crime/vandalism levels may increase due to the urban sprawl encroaching onto
neighbouring properties. It is recommended that the north-western boundary of the
Remainder of Portion 4 of Farm 217 be fenced prior to construction to act as an additional
barrier to prevent unlawful access to Portion 102 of Farm 217.
It has to be noted that the proposed development forms part of the Mossel Bay Municipality‟s
long-term strategy to address the housing need of its area. Not all 616 housing opportunities,
as indicated in the development plan (Appendix B), will be constructed, nor occupied in a
single phase. Housing opportunities will become available as per the funding from the
Municipality. Through conducting an environmental process for more housing opportunities
than which is currently required, the Municipality would be able to address future demand in a
timeous fashion, without having to complete an additional environmental process. (d) Cultural and historic aspects: Heritage Report
The Heritage specialist assessment (Annexure G5) indicated that from a colonial perspective the
proposed development site form part of the early farm Hartenbosch. Historically the farm was
predominantly used for raising livestock.
De Kock (2014) identified no historic structures, ruins or possible gravesites during his fieldwork. Early
aerial photography indicates little cultivation along the Hartenbos River corridor, which include the
northernmost portion of the proposed development site. No significant structures and/or cultural
landscape patterns could be identified through early aerial imagery (De Kock, 2014).
De Kock (2014) recommended that an archaeological impact assessment be undertaken due to the
general sensitive archaeological nature of coastal areas in the Mossel Bay district. It was also stated
that archaeological monitoring may be required during future earthworks and excavations associated
with the proposed development (includes the bulk water pipeline).
Archaeological Impact Assessment (AIA, Nilssen, 2014)
The AIA (Annexure G1) indicated that no significant archaeological resources would be negatively
impacted by the proposed development. The AIA concluded with the following recommended and
required mitigation measures:
Recommended mitigations measures:
Based on the findings of this study and of those in the immediate surroundings, it is
recommended that no further archaeological work or mitigation is required.
Required mitigation measures:
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In the event that vegetation clearing and earthmoving activities expose significant
archaeological materials, such activities must stop and Heritage Western Cape must be
notified immediately.
If archaeological materials are exposed during vegetation clearing and/or earth moving
activities, then they must be dealt with in accordance with the National Heritage Resources
Act (No. 25 of 1999) and at the expense of the developer.
In the event of exposing human remains during construction, the matter will fall into the
domain of Heritage Western Cape (Mr. Guy Thomas) or the South African Heritage Resources
Agency (Mrs Colette Scheermeyer) and will require a professional archaeologist to undertake
mitigation if needed. The developer will be responsible for costs associated with such work.
2. WASTE AND EMISSIONS
(a) Waste (including effluent) management Will the activity produce waste (including rubble) during the construction phase? YES NO If yes, indicate the types of waste (actual type of waste, e.g. oil, and whether hazardous or not) and estimated quantity per type? M3
Limited building rubble. Will the activity produce waste during its operational phase? The activity will generate household effluent and general household waste during its operational phase.
YES NO
If yes, indicate the types of waste (actual type of waste, e.g. oil, and whether hazardous or not) and estimated quantity per type? M3
Where and how will the waste be treated / disposed of (describe)? The project will be serviced with Municipal water borne sewage. Sewage will be disposed of at the
Municipal waste water treatment works. General household waste will be collected as part of the
existing waste removal system currently servicing the Sonskynvallei community. If yes, indicate the types of waste (actual type of waste, e.g. oil, and whether hazardous or not) and estimated quantity per type per phase of the development? Has the municipality or relevant authority confirmed that sufficient capacity exist for treating / disposing of the waste to be generated by this activity(ies)? If yes, provide written confirmation from Municipality or relevant authority. Mossel Bay Municipality is also the Applicant – see Annexure E3 for letter confirming capacity for waste disposal.
YES NO
Will the activity produce waste that will be treated and/or disposed of at another facility other than into a municipal waste stream?
YES NO
If yes, has this facility confirmed that sufficient capacity exist for treating / disposing of the waste to be generated by this activity(ies)? Provide written confirmation from the facility and provide the following particulars of the facility:
YES NO
Does the facility have an operating license? (If yes, please attach a copy of the license.) YES NO
Facility name: Contact person: Postal address: Postal code: Telephone: Cell: E-mail: Fax:
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Describe the measures that will be taken to reduce, reuse or recycle waste: The DEA&DP waste minimisation guideline document for environmental impact assessment reviews
(May, 2003) is the key guideline document regarding management of waste during the construction
period. This Guideline raises awareness to waste minimisation issues and highlights waste and
wastage minimization practices. Part B of this document is of particular importance, as it addresses
issues of general waste and wastage minimization during construction activities. The
recommendations and principles of this document have been used to inform the Environmental
Management Programme (attached in Appendix H).
Mossel Bay Municipality has a „blue-bag‟ recycling programme that is currently running. The
Municipality itself does not recycle the material; the contractor collects the blue bags and then further
proceeds with the recycling process. It is recommended that recyclable materials are sorted at the
source i.e. each individual residence, as it will improve the efficiency of the recycling process.
(b) Emissions into the atmosphere Will the activity produce emissions that will be disposed of into the atmosphere? YES NO If yes, does it require approval in terms of relevant legislation? YES NO Describe the emissions in terms of type and concentration and how it will be treated/mitigated:
3. WATER USE
Please indicate the source(s) of water for the activity by ticking the appropriate box(es)
Municipal Water board Groundwater River, Stream, Dam or Lake Other The activity will not use water
If water is to be extracted from a groundwater source, river, stream, dam, lake or any other natural feature, please indicate the volume that will be extracted per month: N/A Please provide proof of assurance of water supply (eg. Letter of confirmation from municipality / water user associations, yield of borehole) See Annexure E3 for letter from Mossel Bay Municipality confirming water infrastructure capacity. Proposed upgrades in the civil services report. Does the activity require a water use permit / license from DWAF? YES NO If yes, please submit the necessary application to Department of Water Affairs and attach proof thereof to this application. Describe the measures that will be taken to reduce water demand, and measures to reuse or recycle water: Dual flush toilets must be installed. Low flow showerheads and taps must be installed.
It is unlikely that the available project financing will cover rainwater storage tanks therefore such are
not recommended as it is unlikely to be feasible.
The beneficiaries that qualify for the subsidised houses are allocated a limited volume of „free‟ water
for which they do not pay (it is subsidised by the State). As soon as they exceed their „free‟ monthly
allocation they have to pay for the water they use. As a result such low income households rarely
exceed their „free‟ monthly volume which is a default water saving mechanism in itself.
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4. POWER SUPPLY
Please indicate the source of power supply eg. Municipality / Eskom / Renewable energy source Municipal (Annexure E2) If power supply is not available, where will power be sourced from?
4.1 ENERGY EFFICIENCY Describe the design measures, if any, that have been taken to ensure that the activity is energy efficient: The use of low voltage or compact fluorescent lights (instead of incandescent globes) is
recommended for each unit.
It is doubtful whether project funding will be sufficient to allow solar heating technologies to be
implemented, but should funding be available, it is recommended that heat pumps or roof set solar
panels be installed as a measure to reduce electricity consumption.
Describe how alternative energy sources have been taken into account or been built into the design of the activity, if any: As described above, solar power technologies must be explored if funding is available.
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5. DESCRIPTION AND ASSESSMENT OF THE SIGNIFICANCE OF IMPACTS PRIOR TO AND AFTER MITIGATION
Please note: While sections are provided for impacts on certain aspects of the environment and certain impacts, the sections should also be copied and completed for all other impacts.
(a) Impacts that may result from the planning, design and construction phase (briefly describe and compare the potential impacts (as appropriate), significance rating of impacts, proposed
mitigation and significance rating of impacts after mitigation that are likely to occur as a result of the planning, design and construction phase. Potential impacts on geographical and physical aspects: Exposure of soil during construction. Transformation of area from natural to transformed
Alternative 1 Alternative 2 (preferred) Alternative 3 (No-Go)
Nature of impact: Negative Negative Positive (no exposure of soil and transformation of proposed development area)
Extent and duration of impact: Local, permanent (development footprint)
Local, permanent (development footprint) Local, long term
Probability of occurrence: Definite Definite Probable Degree to which the impact can be reversed: Low Low Positive – no need to reverse Degree to which the impact may cause irreplaceable loss of resources: Medium Medium Low
Cumulative impact prior to mitigation: Medium Medium No need to mitigate Significance rating of impact prior to mitigation (Low, Medium, Medium-High, High, or Very-High)
Medium Medium N/A
Degree to which the impact can be mitigated: High High N/A
Proposed mitigation:
Construction area to be clearly demarcated prior to construction to avoid encroachment into adjacent areas. No activities allowed within the No-Go area.
Environmental Control Officer
Construction area to be clearly demarcated prior to construction to avoid encroachment into adjacent areas. No activities allowed within the No-Go area.
Environmental Control Officer
N/A
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(ECO) must monitor construction activities
(ECO) must monitor construction activities
Cumulative impact post mitigation: Low Low N/A Significance rating of impact after mitigation (Low, Medium, Medium-High, High, or Very-High)
Low Low N/A
Potential impacts on geographical and physical aspects: Construction of a ±1.4km bulk water pipeline from Hartenboskop reservoir, over a drainage line and to the proposed development
Alternative 1 Alternative 2 (preferred) Alternative 3 (No-Go)
Nature of impact:
Negative Construction of the bulk water pipeline will follow the alignment of an existing pipeline i.e. the proposed new pipeline will be installed adjacent to the existing one and follow the same footprint where possible.
Neutral Realignment of a section of the water pipeline to avoid an area indicated as sensitive will reduce the potential impact on the receiving environment.
Neutral (no impact) Current capacity of pipeline may limit future development.
Extent and duration of impact: Specific to alignment, long term (development footprint)
Specific to alignment, long term (development footprint) N/A
Probability of occurrence: Definite Definite N/A Degree to which the impact can be reversed: Low Low N/A
Degree to which the impact may cause irreplaceable loss of resources:
Medium-High (within the NFEPA area)
Negligible (following existing servitude and gravel track already transformed).
N/A
Cumulative impact prior to mitigation: Medium Very Low N/A Significance rating of impact prior to mitigation (Low, Medium, Medium-High, High, or Very-High)
High-Medium (mainly crossing of NFEPA area) Very Low (avoiding sensitive section) N/A
Degree to which the impact can be mitigated: Low High N/A
Proposed mitigation: Construction area to be
clearly demarcated prior to construction to avoid
Sensitive area avoided. Construction area to be
clearly demarcated prior to N/A
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encroachment into adjacent areas. No activities allowed within the No-Go area;
Environmental Control Officer (ECO) must monitor construction activities; and
Drainage line crossing must be carefully monitored for erosion, damage to banks and littering.
construction to avoid encroachment into adjacent areas. No activities allowed within the No-Go area;
Environmental Control Officer (ECO) must monitor construction activities; and
Drainage line crossing must be carefully monitored for erosion, damage to banks and littering.
Cumulative impact post mitigation: Medium Low N/A Significance rating of impact after mitigation (Low, Medium, Medium-High, High, or Very-High)
Medium Low N/A
Potential impact on biological aspects: Removal of Vegetation for the construction of housing opportunities
Alternative 1 Alternative 2 (preferred) Alternative 3 (No-Go)
Nature of impact: Negative Negative Positive (no loss of vegetation) Extent and duration of impact: Local, Permanent Local, Permanent N/A Probability of occurrence: Definite Definite N/A
Degree to which the impact can be reversed: Low (construction of housing opportunities needs to occur)
Low (construction of housing opportunities needs to occur)
N/A
Degree to which the impact may cause irreplaceable loss of resources:
Medium (layout does not reflect botanically sensitive areas)
Low (additional areas with conservation worthy vegetation has been avoided in the layout)
N/A
Cumulative impact prior to mitigation: Medium Medium-Low N/A Significance rating of impact prior to mitigation (Low, Medium, Medium-High, High, or Very-High)
Medium Medium N/A
Degree to which the impact can be mitigated: Medium Medium-High N/A
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Proposed mitigation:
Demarcate no-go zones to avoid encroachment into natural areas surrounding the development site;
Use natural, locally indigenous, vegetation for landscaping;
Appoint an ECO during construction; and
Consult Environmental Management Programme which forms part of this report.
Layout amended to avoid sensitive areas.
Demarcate no-go zones to avoid encroachment into natural areas surrounding the development site;
Use natural, locally indigenous, vegetation for landscaping;
Appoint an ECO during construction; and
Consult Environmental Management Programme which forms part of this report.
N/A
Cumulative impact post mitigation: Low Low N/A Significance rating of impact after mitigation (Low, Medium, Medium-High, High, or Very-High)
Low Low N/A
Potential impact on biological aspects: Irreplaceable loss of the thicket component of the Herbertsdale Renoster Thicket due to housing construction (Coetzee, 2014).
Alternative 1 Alternative 2 (preferred) Alternative 3 (No-Go)
Nature of impact: Negative Negative Positive (no loss of vegetation) Extent and duration of impact: Local, Permanent Local, Permanent N/A Probability of occurrence: Definite Definite N/A Degree to which the impact can be reversed: Irreversible Irreversible N/A Degree to which the impact may cause irreplaceable loss of resources: High Medium N/A
Cumulative impact prior to mitigation: High Medium N/A Significance rating of impact prior to mitigation (Low, Medium, Medium-High, High, or Very-High)
High Low N/A
Degree to which the impact can be mitigated: Low High N/A
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Proposed mitigation:
Demarcate no-go zones to avoid encroachment into natural areas surrounding the development site;
Use natural, locally indigenous, vegetation for landscaping;
Appoint an ECO during construction; and
Consult Environmental Management Programme which forms part of this report.
Exclude thicket area on north-western boundary of development area;
Off-setting the impact by conserving the undisturbed area south of the proposed development site should be considered;
Demarcate no-go zones to avoid encroachment into natural areas surrounding the development site;
Use natural, locally indigenous, vegetation for landscaping;
Appoint an ECO during construction; and
Consult Environmental Management Programme which forms part of this report.
N/A
Cumulative impact post mitigation: Medium-high Very Low N/A Significance rating of impact after mitigation (Low, Medium, Medium-High, High, or Very-High)
Medium-high Very Low N/A
Potential impact on biological aspects: Irreplaceable loss of the Renosterveld component of the Herbertsdale Renoster Thicket due to housing construction (Coetzee, 2014).
Alternative 1 Alternative 2 (preferred) Alternative 3 (No-Go)
Nature of impact: Negative Negative Positive (no loss of vegetation) Extent and duration of impact: Local, Permanent Local, Permanent N/A Probability of occurrence: Definite Definite N/A
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Degree to which the impact can be reversed: Irreversible Irreversible N/A Degree to which the impact may cause irreplaceable loss of resources: High High N/A
Cumulative impact prior to mitigation: High High N/A Significance rating of impact prior to mitigation (Low, Medium, Medium-High, High, or Very-High)
High High N/A
Degree to which the impact can be mitigated: Medium-low Medium N/A
Proposed mitigation:
Demarcate no-go zones to avoid encroachment into natural areas surrounding the development site;
Use natural, locally indigenous, vegetation for landscaping;
Appoint an ECO during construction; and
Consult Environmental Management Programme which forms part of this report.
Off-setting the impact by conserving the undisturbed area south of the proposed development site should be considered;
Demarcate no-go zones to avoid encroachment into natural areas surrounding the development site;
Use natural, locally indigenous, vegetation for landscaping;
Appoint an ECO during construction; and
Consult Environmental Management Programme which forms part of this report.
N/A
Cumulative impact post mitigation: Medium Low N/A Significance rating of impact after mitigation (Low, Medium, Medium-High, High, or Very-High)
Medium Low N/A
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Potential impact on biological aspects: Impact on vegetation due to construction of bulk water pipeline
Alternative 1 Alternative 2 (preferred alignment –
as recommended by Botanical Specialist (Coetzee, 2014)
Alternative 3 (No-Go)
Nature of impact: Negative Negative No impact Extent and duration of impact: Local, Medium term Local, Medium term N/A Probability of occurrence: Definite Definite N/A Degree to which the impact can be reversed: Medium (partially reversible) Medium (partially reversible) N/A Degree to which the impact may cause irreplaceable loss of resources: Medium Very Low N/A
Cumulative impact prior to mitigation: Medium Low N/A Significance rating of impact prior to mitigation (Low, Medium, Medium-High, High, or Very-High)
Medium-High Low N/A
Degree to which the impact can be mitigated: Medium High N/A
Proposed mitigation:
Demarcate no-go zones to avoid encroachment into natural areas surrounding the development site;
Use natural, locally indigenous, vegetation for landscaping;
Appoint an ECO during construction; and
Consult Environmental Management Programme which forms part of this report.
Route the pipeline all along the edge of the existing road up to the reservoir to avoid sensitive NFEPA area.
Demarcate no-go zones to avoid encroachment into natural areas surrounding the development site;
Use natural, locally indigenous, vegetation for landscaping;
Appoint an ECO during construction; and
Consult Environmental Management Programme which forms part of this report.
N/A
Cumulative impact post mitigation: Medium Low N/A Significance rating of impact after mitigation (Low, Medium, Medium-High, High, or Very-High)
Medium negative Low positive N/A
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Potential impact on biological aspects: Disruption of important landscape connectivity (Coetzee, 2014).
Alternative 1 Alternative 2 (preferred) Alternative 3 (No-Go)
Nature of impact: Negative Negative No impact on connectivity Extent and duration of impact: Local, Permanent Local, Permanent N/A Probability of occurrence: Improbable Improbable N/A Degree to which the impact can be reversed: No impact No impact N/A Degree to which the impact may cause irreplaceable loss of resources: Low Low N/A
Cumulative impact prior to mitigation: Low Low N/A Significance rating of impact prior to mitigation (Low, Medium, Medium-High, High, or Very-High)
Low Low N/A
Degree to which the impact can be mitigated: No mitigation necessary No mitigation necessary N/A
Proposed mitigation: Connectivity not disrupted –
no mitigation necessary Connectivity not disrupted – no
mitigation necessary N/A
Cumulative impact post mitigation: Low Low N/A Significance rating of impact after mitigation (Low, Medium, Medium-High, High, or Very-High)
Low Low N/A
Potential impacts on socio-economic aspects: Crime during construction period
Alternative 1 Alternative 2 (preferred) Alternative 3 (No-Go)
Nature of impact: Negative Negative Positive
Extent and duration of impact: Local, short term (during civil construction phase)
Local, short term (during civil construction phase) Local, Long term
Probability of occurrence: Improbable to probable Improbable to probable Improbable (no direct correlation between crime and construction of new housing opportunities)
Degree to which the impact can be reversed: High High Positive – no need to reverse Degree to which the impact may cause irreplaceable loss of resources: Low Low Low
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Cumulative impact prior to mitigation: Medium Medium Medium Significance rating of impact prior to mitigation (Low, Medium, Medium-High, High, or Very-High)
Low Low Low
Degree to which the impact can be mitigated: High High No need to mitigate
Proposed mitigation:
Contractors may not move off-site; and
No overnight facilities may be allowed
Contractors may not move off-site; and
No overnight facilities may be allowed.
N/A
Cumulative impact post mitigation: Low Low N/A Significance rating of impact after mitigation (Low, Medium, Medium-High, High, or Very-High)
Low Low N/A
Potential impacts on socio-economic aspects: Employment opportunities and generation of income.
Alternative 1 Alternative 2 (preferred) Alternative 3 (No-Go)
Nature of impact: Positive Positive Negative
Extent and duration of impact: Local, Short term (during civil construction phase)
Local, Short term (during civil construction phase) Local, long term
Probability of occurrence: Medium Medium Medium Degree to which the impact can be reversed: Positive – no need to reverse Positive – no need to reverse Low Degree to which the impact may cause irreplaceable loss of resources: Low Low Low
Cumulative impact prior to mitigation: Medium Medium Medium Significance rating of impact prior to mitigation (Low, Medium, Medium-High, High, or Very-High)
Low Low Low
Degree to which the impact can be mitigated: Medium-High Medium-High Medium-High
Proposed mitigation:
The Applicant must apply a „local first‟ policy when appointing contractors to ensure that maximum employment opportunities are offered to the local community (Sonskynvallei), the area (Mossel
The Applicant must apply a „local first‟ policy when appointing contractors to ensure that maximum employment opportunities are offered to the local community (Sonskynvallei), the area (Mossel Bay) and the region (Garden
Construction of the proposed housing development. This will provide job opportunities to the community, area and region.
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Bay) and the region (Garden Route. Route. Cumulative impact post mitigation: Medium-High Medium-High Medium-High Significance rating of impact after mitigation (Low, Medium, Medium-High, High, or Very-High)
Medium Medium Medium
Potential impacts on cultural-historical aspects:
The Heritage assessment conducted by De Kock (2014) stated that no heritage resources would be negatively impacted by the proposed development. The report did however recommend that an archaeological impact assessment be conducted due to the sensitive archaeological nature of the Moseel Bay coastal district. This impact table therefore focuses on the archaeological impacts associated with the proposed development, as per the archaeological impact assessment report compiled by Nilssen (2014).
Alternative 1 Alternative 2 (preferred) Alternative 3 (No-Go)
Nature of impact: Negligible Negligible Neutral Extent and duration of impact: Local, permanent Local, permanent N/A Probability of occurrence: Low to none Low to none N/A
Degree to which the impact can be reversed: Low (very little impact; housing development will be permanent)
Low (very little impact; housing development will be permanent) N/A
Degree to which the impact may cause irreplaceable loss of resources: Low Low N/A
Cumulative impact prior to mitigation: Low Low N/A Significance rating of impact prior to mitigation (Low, Medium, Medium-High, High, or Very-High)
Low Low N/A
Degree to which the impact can be mitigated: Low (very little impact – no impact on significant archaeological resources)
Low (very little impact – no impact on significant archaeological resources) N/A
Proposed mitigation:
No further archaeological work or mitigation is needed;
Uncovering of significant archaeological materials or human remains must be dealt with as indicated in the AIA
No further archaeological work or mitigation is needed;
Uncovering of significant archaeological materials or human remains must be dealt with as indicated in the AIA
N/A
Cumulative impact post mitigation: Low Low N/A Significance rating of impact after mitigation Low Low N/A
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(Low, Medium, Medium-High, High, or Very-High)
Potential noise impacts: Construction Noise Alternative 1 Alternative 2 (preferred) Alternative 3 (No-Go)
Nature of impact: Negative Negative No impact
Extent and duration of impact: Local, short term/temporary (during construction phase)
Local, short term/temporary (during construction phase) N/A
Probability of occurrence: High High N/A Degree to which the impact can be reversed: Low Low N/A Degree to which the impact may cause irreplaceable loss of resources: Low Low N/A
Cumulative impact prior to mitigation: Medium Medium N/A Significance rating of impact prior to mitigation (Low, Medium, Medium-High, High, or Very-High)
Medium-High Medium-High N/A
Degree to which the impact can be mitigated: Medium Medium N/A
Proposed mitigation:
1) Construction activities must be limited to 7:00-18:00 during working days, 8:00 – 14:00 on Saturdays and no construction activities allowed on Sundays and Public Holidays. This must be monitored by the ECO.
2) Construction vehicles must abide by the EMP Noise Emission requirements.
1) Construction activities must be limited to 7:00-18:00 during working days, 8:00 – 14:00 on Saturdays and no construction activities allowed on Sundays and Public Holidays. This must be monitored by the ECO.
2) Construction vehicles must abide by the EMP Noise Emission requirements.
N/A
Cumulative impact post mitigation: Low Low N/A Significance rating of impact after mitigation (Low, Medium, Medium-High, High, or Very-High)
Low Low N/A
Potential visual impacts: Transformation of a vacant site to a developed area (exposure of soil during construction)
Alternative 1 Alternative 2 (preferred) Alternative 3 (No-Go)
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Nature of impact: Low negative Low negative No impact Extent and duration of impact: Site specific, permanent Site specific, permanent N/A Probability of occurrence: Probable Probable N/A Degree to which the impact can be reversed: Negligible Negligible N/A Degree to which the impact may cause irreplaceable loss of resources:
Low (impact considered insignificant) Low (impact considered insignificant) N/A
Cumulative impact prior to mitigation: Low Low N/A Significance rating of impact prior to mitigation (Low, Medium, Medium-High, High, or Very-High)
Low Low N/A
Degree to which the impact can be mitigated: Low Low N/A
Proposed mitigation:
Do not clear the entire development site at once. Clear sections as is needed. This will decrease the visual impact during the construction phase
Do not clear the entire development site at once. Clear sections as is needed. This will decrease the visual impact during the construction phase
N/A
Cumulative impact post mitigation: Low Low N/A Significance rating of impact after mitigation (Low, Medium, Medium-High, High, or Very-High)
Low Low N/A
(b) Impacts that may result from the operational phase (briefly describe and compare the potential impacts (as appropriate), significance rating of impacts, proposed mitigation and
significance rating of impacts after mitigation that are likely to occur as a result of the operational phase.
Potential impacts on the geographical and physical aspects: Change in character from vacant property to urban township
Alternative 1 Alternative 2 (preferred) Alternative 3 (No-Go)
Nature of impact: Negative Negative No impact Extent and duration of impact: Local, Permanent Local, Permanent N/A Probability of occurrence: High High N/A Degree to which the impact can be reversed: Low Low N/A Degree to which the impact may cause irreplaceable loss of resources: Low Low N/A
Cumulative impact prior to mitigation: Medium Low N/A
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Significance rating of impact prior to mitigation (Low, Medium, Medium-High, High, or Very-High)
Medium Low N/A
Degree to which the impact can be mitigated: Medium Low N/A
Proposed mitigation: Reduce bulk by introducing different typologies No further mitigation N/A
Cumulative impact post mitigation: Medium Low N/A Significance rating of impact after mitigation (Low, Medium, Medium-High, High, or Very-High)
Medium Low N/A
Potential impact biological aspects: Littering, damage to vegetation and harvesting of vegetation (fire wood)
Alternative 1 Alternative 2 (preferred) Alternative 3 (No-Go)
Nature of impact: Negative Negative
Neutral – no additional impact, however it is anticipated that, to a degree, this impact is already occurring.
Extent and duration of impact: Local, long term Local, long term Local, long term Probability of occurrence: Probable Probable Probable
Degree to which the impact can be reversed: Medium (if the community can take ownership of their surrounding environment and conserve it)
Medium (if the community can take ownership of their surrounding environment and conserve it)
Medium (if the community can take ownership of their surrounding environment and conserve it)
Degree to which the impact may cause irreplaceable loss of resources: Low Low Low
Cumulative impact prior to mitigation: Medium Medium Medium Significance rating of impact prior to mitigation (Low, Medium, Medium-High, High, or Very-High)
Medium Medium Medium
Degree to which the impact can be mitigated: Medium Medium Medium
Proposed mitigation: Littering can be mitigated by
placing enough rubbish bins Littering can be mitigated by
placing enough rubbish bins Littering can be mitigated by
placing enough rubbish bins
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throughout the proposed new development. Bins must be well indicated;
Signage explaining the negative effects of littering (environmental education); and
This issue will best be addressed when the community takes ownership of the natural environment surrounding them.
throughout the proposed new development. Bins must be well indicated;
Signage explaining the negative effects of littering (environmental education); and
This issue will best be addressed when the community takes ownership of the natural environment surrounding them.
throughout the proposed new development. Bins must be well indicated;
Signage explaining the negative effects of littering (environmental education); and
This issue will best be addressed when the community takes ownership of the natural environment surrounding them.
Cumulative impact post mitigation: Low Low Low Significance rating of impact after mitigation (Low, Medium, Medium-High, High, or Very-High)
Low Low Low
Potential impact on biological aspects: Indirect off-site human impact in unaffected natural vegetation due to the close proximity to the proposed development (Coetzee, 2014).
Alternative 1 Alternative 2 (preferred) Alternative 3 (No-Go)
Nature of impact: Negative Negative No additional impact Extent and duration of impact: Local, Permanent Local, Permanent N/A Probability of occurrence: Probable Probable N/A Degree to which the impact can be reversed: Medium (partially reversible) Medium (partially reversible) N/A Degree to which the impact may cause irreplaceable loss of resources: Medium Medium N/A
Cumulative impact prior to mitigation: Medium Medium N/A Significance rating of impact prior to mitigation (Low, Medium, Medium-High, High, or Very-High)
Medium Medium N/A
Degree to which the impact can be mitigated: Medium Medium N/A
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Proposed mitigation:
Fencing can restrict access to natural areas;
Educate residents; and Constant clean-up actions
Fencing can restrict access to natural areas;
Educate residents; and Constant clean-up actions
N/A
Cumulative impact post mitigation: Low Low N/A Significance rating of impact after mitigation (Low, Medium, Medium-High, High, or Very-High)
Low Low N/A
Potential impact biological aspects: Damage to watercourse and vegetation as a result of maintenance of new bulk water pipeline
Alternative 1 Alternative 2 (preferred) Alternative 3 (No-Go)
Nature of impact: Negative Negative
No impact. If the new pipeline is not constructed there will be no impact. Maintenance of the old pipeline will still have to occur, however the impacts of the old pipeline is not assessed as part of this application.
Extent and duration of impact: Local, periodical (as is needed) Local, periodical (as is needed) N/A
Probability of occurrence:
Probable (pipeline is underground and will need to be exposed for maintenance; dynamic nature of a watercourse may result in damage to infrastructure)
Unlikely with portion of pipeline realigned to avoid NFEPA section. N/A
Degree to which the impact can be reversed: Low Low N/A Degree to which the impact may cause irreplaceable loss of resources: High Low N/A
Cumulative impact prior to mitigation: Medium Low N/A
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Significance rating of impact prior to mitigation (Low, Medium, Medium-High, High, or Very-High)
Medium Low N/A
Degree to which the impact can be mitigated: Medium High N/A
Proposed mitigation:
Maintenance area to be clearly demarcated prior to construction to avoid encroachment into adjacent areas;
Environmental Control Officer (ECO) must monitor maintenance activities; and
Drainage line crossing must be carefully monitored for erosion, damage to banks and littering.
Avoid NFEPA area completely Maintenance area to be clearly
demarcated prior to construction to avoid encroachment into adjacent areas;
Environmental Control Officer (ECO) must monitor maintenance activities; and
Drainage line crossing must be carefully monitored for erosion, damage to banks and littering.
N/A
Cumulative impact post mitigation: Low Low N/A Significance rating of impact after mitigation (Low, Medium, Medium-High, High, or Very-High)
Low Low N/A
Potential impacts on the socio-economic aspects: Providing housing opportunities in an area with a housing need.
Alternative 1 Alternative 2 (preferred) Alternative 3 (No-Go)
Nature of impact: Positive Positive Negative
Extent and duration of impact: Local, permanent Local, permanent Local, permanent (no development will result in no housing opportunities)
Probability of occurrence: Definite Definite Definite Degree to which the impact can be reversed: Positive – no need to be reversed Positive – no need to be reversed Low Degree to which the impact may cause irreplaceable loss of resources: Low Low Low
Cumulative impact prior to mitigation: High High High negative Significance rating of impact prior to mitigation High High High negative
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(Low, Medium, Medium-High, High, or Very-High) Degree to which the impact can be mitigated: Positive – no mitigation Positive – no mitigation High
Proposed mitigation: Positive – no mitigation Positive – no mitigation
Follow correct procedures (e.g. environmental and planning processes) and implement housing development.
Cumulative impact post mitigation: Positive – no mitigation Positive – no mitigation Low Significance rating of impact after mitigation (Low, Medium, Medium-High, High, or Very-High)
Positive – no mitigation Positive – no mitigation Low
Potential impacts on the socio-economic aspects: Potential for increase in crime, theft, vandalism and reduced security levels within the general area.
Alternative 1 Alternative 2 (preferred) Alternative 3 (No-Go)
Nature of impact: Negative Negative Neutral – no additional impact. Extent and duration of impact: Local, long term Local, long term N/A Probability of occurrence: Probable Probable N/A Degree to which the impact can be reversed: Low Low N/A Degree to which the impact may cause irreplaceable loss of resources: Medium Medium N/A
Cumulative impact prior to mitigation: Medium-High Medium-High N/A Significance rating of impact prior to mitigation (Low, Medium, Medium-High, High, or Very-High)
Medium-High Medium-High N/A
Degree to which the impact can be mitigated: Low Low N/A
Proposed mitigation:
Retailers / Operators in the area must be vigilant and incidents of crime/theft must be reported to the local Police; and
Neighbourhood watch.
Retailers / Operators in the area must be vigilant and incidents of crime/theft must be reported to the local Police; and
Neighbourhood watch.
N/A
Cumulative impact post mitigation: Medium Medium N/A
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Significance rating of impact after mitigation (Low, Medium, Medium-High, High, or Very-High)
Medium Medium N/A
Potential impacts on the cultural-historical aspects:
The Heritage assessment conducted by De Kock (2014) stated that no heritage resources would be negatively impacted by the proposed development. The report did however recommend that an archaeological impact assessment be conducted due to the sensitive archaeological nature of the Moseel Bay coastal district. This impact table therefore focuses on the archaeological impacts associated with the proposed development, as per the archaeological impact assessment report compiled by Nilssen (2014).
Alternative 1 Alternative 2 (preferred – specialist
recommendations taken into account)
Alternative 3 (No-Go)
Nature of impact: Negligible Negligible No impact Extent and duration of impact: Local, permanent Local, permanent N/A Probability of occurrence: Low to none Low to none N/A
Degree to which the impact can be reversed: Low (very little impact; housing development will be permanent)
Low (very little impact; housing development will be permanent)
N/A
Degree to which the impact may cause irreplaceable loss of resources: Low Low N/A
Cumulative impact prior to mitigation: Low Low N/A Significance rating of impact prior to mitigation (Low, Medium, Medium-High, High, or Very-High)
Low Low N/A
Degree to which the impact can be mitigated: Low (very little impact – no impact on significant archaeological resources)
Low (very little impact – no impact on significant archaeological resources)
N/A
Proposed mitigation:
No further archaeological work or mitigation is needed;
Uncovering of significant archaeological materials or human remains must be dealt with as indicated in the AIA
No further archaeological work or mitigation is needed;
Uncovering of significant archaeological materials or human remains must be dealt with as indicated in the AIA
N/A
Cumulative impact post mitigation: Low Low N/A
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Significance rating of impact after mitigation (Low, Medium, Medium-High, High, or Very-High)
Low Low N/A
Potential visual impacts: Transformation of a vacant site to a developed area
Alternative 1 Alternative 2 (preferred) Alternative 3 (No-Go)
Nature of impact: Very low negative Negligible to very low negative No impact
Extent and duration of impact: Extent: Zone of Visual Influence is approximately 3km. Duration: Permanent
Extent: Zone of Visual Influence is approximately 3km. Duration: Permanent
N/A
Probability of occurrence: Definite Definite N/A Degree to which the impact can be reversed: Low Low N/A Degree to which the impact may cause irreplaceable loss of resources:
Low (impact considered insignificant) Low (impact considered insignificant) N/A
Cumulative impact prior to mitigation: Medium Low (with semi-detached mixture) N/A Significance rating of impact prior to mitigation (Low, Medium, Medium-High, High, or Very-High)
Medium Low N/A
Degree to which the impact can be mitigated: Medium Low N/A
Proposed mitigation:
Reduce skyline intrusion by relocating units 18 – 27 off the prominent ridgeline, as seen from the R328 road receptors;
The dwellings should be painted in a grey-green colour range to reduce visual intrusion as seen from the N2 and Hartenbosheuwels residential areas;
Dust control measures should be implemented during construction;
Indigenous and endemic
Reduce skyline intrusion by relocating units 18 – 27 off the prominent ridgeline, as seen from the R328 road receptors;
Utilization of the semi-detached dwelling option so as to reduce the visual footprint of development and create an appearance of more open space;
The dwellings should be painted in a grey-green colour range to reduce visual intrusion as seen from the N2 and Hartenbosheuwels
N/A
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trees should be incorporated into the street design;
Overhead mast lighting should not be utilised; and
Street lighting should be downward directional.
residential areas; Dust control measures should
be implemented during construction;
Indigenous and endemic trees should be incorporated into the street design;
Overhead mast lighting should not be utilised; and
Street lighting should be downward directional.
Cumulative impact post mitigation: Low Very low to negligible N/A Significance rating of impact after mitigation (Low, Medium, Medium-High, High, or Very-High)
Low Very low (insignificant) N/A
(c) Impacts that may result from the decommissioning and closure phase (briefly describe and compare the potential impacts (as appropriate), significance rating of impacts, proposed mitigation
and significance rating of impacts after mitigation that are likely to occur as a result of the decommissioning and closure phase. The project is of a permanent nature. It is unlikely that the housing development, once established, will be decommissioned in the near future. No impacts identified/assessed as such.
Potential impacts on the geographical and physical aspects: Alternative 1 Alternative 2 (preferred) Alternative 3 (No-Go)
Nature of impact: Extent and duration of impact: Probability of occurrence: Degree to which the impact can be reversed: Degree to which the impact may cause irreplaceable loss of resources:
Cumulative impact prior to mitigation: Significance rating of impact prior to mitigation
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(Low, Medium, Medium-High, High, or Very-High) Degree to which the impact can be mitigated: Proposed mitigation: Cumulative impact post mitigation: Significance rating of impact after mitigation (Low, Medium, Medium-High, High, or Very-High)
Potential impact biological aspects: Alternative 1 Alternative 2 (preferred) Alternative 3 (No-Go) Nature of impact: Extent and duration of impact: Probability of occurrence: Degree to which the impact can be reversed: Degree to which the impact may cause irreplaceable loss of resources:
Cumulative impact prior to mitigation: Significance rating of impact prior to mitigation (Low, Medium, Medium-High, High, or Very-High)
Degree to which the impact can be mitigated: Proposed mitigation: Cumulative impact post mitigation: Significance rating of impact after mitigation (Low, Medium, Medium-High, High, or Very-High)
Potential impacts on the socio-economic aspects: Alternative 1 Alternative 2 (preferred) Alternative 3 (No-Go)
Nature of impact: Extent and duration of impact: Probability of occurrence: Degree to which the impact can be reversed: Degree to which the impact may cause irreplaceable loss of resources:
Cumulative impact prior to mitigation:
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Significance rating of impact prior to mitigation (Low, Medium, Medium-High, High, or Very-High)
Degree to which the impact can be mitigated: Proposed mitigation: Cumulative impact post mitigation: Significance rating of impact after mitigation (Low, Medium, Medium-High, High, or Very-High)
Potential impacts on the cultural-historical aspects: Alternative 1 Alternative 2 (preferred) Alternative 3 (No-Go)
Nature of impact: Extent and duration of impact: Probability of occurrence: Degree to which the impact can be reversed: Degree to which the impact may cause irreplaceable loss of resources:
Cumulative impact prior to mitigation: Significance rating of impact prior to mitigation (Low, Medium, Medium-High, High, or Very-High)
Degree to which the impact can be mitigated: Proposed mitigation: Cumulative impact post mitigation: Significance rating of impact after mitigation (Low, Medium, Medium-High, High, or Very-High)
Potential noise impacts: Alternative 1 Alternative 2 (preferred) Alternative 3 (No-Go) Nature of impact: Extent and duration of impact: Probability of occurrence: Degree to which the impact can be reversed: Degree to which the impact may cause irreplaceable loss of resources:
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Cumulative impact prior to mitigation: Significance rating of impact prior to mitigation (Low, Medium, Medium-High, High, or Very-High)
Degree to which the impact can be mitigated: Proposed mitigation: Cumulative impact post mitigation: Significance rating of impact after mitigation (Low, Medium, Medium-High, High, or Very-High)
Potential visual impacts: Alternative 1 Alternative 2 (preferred) Alternative 3 (No-Go) Nature of impact: Extent and duration of impact: Probability of occurrence: Degree to which the impact can be reversed: Degree to which the impact may cause irreplaceable loss of resources:
Cumulative impact prior to mitigation: Significance rating of impact prior to mitigation (Low, Medium, Medium-High, High, or Very-High)
Degree to which the impact can be mitigated: Proposed mitigation: Cumulative impact post mitigation: Significance rating of impact after mitigation (Low, Medium, Medium-High, High, or Very-High)
(d) Any other impacts: Potential impact: Alternative 1 Alternative 2 (preferred) Alternative 3 (No-Go) Nature of impact: Extent and duration of impact: Probability of occurrence: Degree to which the impact can be reversed: Degree to which the impact may cause
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irreplaceable loss of resources: Cumulative impact prior to mitigation: Significance rating of impact prior to mitigation (Low, Medium, Medium-High, High, or Very-High)
Degree to which the impact can be mitigated: Proposed mitigation: Cumulative impact post mitigation: Significance rating of impact after mitigation (Low, Medium, Medium-High, High, or Very-High)
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6. SPECIALIST INPUTS/STUDIES AND RECOMMENDATIONS
Please note: Specialist inputs/studies must be attached to this report as Appendix G. Also take into account the Department‟s Guidelines on the Involvement of Specialists in EIA Processes available on the Department‟s website (http://www.capegateway.gov.za/eadp).
Specialist inputs/studies and recommendations:
Archaeological The AIA (Annexure G1) indicated that no significant archaeological
resources would be negatively impacted by the proposed development.
The AIA concluded with the following recommended and required mitigation
measures:
Recommended mitigations measures:
Based on the findings of this study and of those in the
immediate surroundings, it is recommended that no further
archaeological work or mitigation is required.
Required mitigation measures:
In the event that vegetation clearing and earthmoving activities
expose significant archaeological materials, such activities must
stop and Heritage Western Cape must be notified immediately.
If archaeological materials are exposed during vegetation clearing
and/or earth moving activities, then they must be dealt with in
accordance with the National Heritage Resources Act (No. 25 of
1999) and at the expense of the developer.
In the event of exposing human remains during construction, the
matter will fall into the domain of Heritage Western Cape (Mr. Guy
Thomas) or the South African Heritage Resources Agency (Mrs
Colette Scheermeyer) and will require a professional archaeologist
to undertake mitigation if needed. The developer will be
responsible for costs associated with such work
Botanical
(Coetzee, 2014)
The vegetation of the proposed development site is classified as described
as Groot Brak Dune Strandveld and classified as ‘Endangered’ in terms
of ecosystem status, and ‘not protected’ in terms of protection status. This
vegetation type is associated with flat undulating landscapes and steep
coastal slopes.
At a finer scale the vegetation has been described as Herbertsdale
Renoster Thicket which is characterised by small thicket clumps occurring
in a matrix of Renosterveld. The Renosterveld component of the vegetation
is very grassy in the areas most recently burnt. True thicket occurs west of
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the rugby field along the north-western border of the development site.
This area has been identified by the Botanical specialist as conservation
worthy and recommended to be excluded from the development area. The
preferred layout assessed in this document reflects the specialist‟s
recommendation.
Furthermore the specialist recommends that the natural area south and
west of the development site be set aside as a conservation area to offset
the impact of the much needed housing development.
The proposed development area is not a part of any important landscape
corridor and its impact on landscape connectivity is consequently
considered to be of low significance.
The proposed alignment of the bulk water supply pipeline will result in
unnecessary natural habitat destruction, as it will impact on a part of the
more sensitive thicket area. With the proposed mitigation, the overall
impact will be very low or negligible. As mitigation, it is alternatively
proposed that the pipeline be aligned along the road up to the water
storage reservoir to the south to avoid the NFEPA section. See Annexure
G2.
Civil Services Report
(Du Preez, 2014)
The following conclusion are from the Civil Services Report (Annexure G3):
Water for the proposed development cannot be provided by
connecting to the existing municipal network. A new 1200lk
reservoir at the Hartenboskop reservoir site and a 200mm dia bulk
water connection will be required from this reservoir. Cost
estimates are provided in the text above.
Sewage flow from the proposed development can be
accommodated in the existing network of the adjacent
Sonskynvallei residential area. An additional internal sewage pump
station and sewage line rising main is required. No dedicated bulk
sewer outfall connections are required.
The stormwater generated by the development will be managed
within the site to ensure the runoff rates for the full spectrum of
design storms do not exceed the runoff rates from the pre-
developed site, where feasible. The minor storms will be managed
within the formal stormwater system comprising inlets, channels
and pipes. The major storms will be conveyed and managed
overland via the roads and public open spaces. Typical stormwater
discharge structures, with incorporated erosion protection
measures, have been detailed in Annexure A of the Civil Services
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Report.
Waste generated by the development will be collected and
managed by Mossel Bay Municipality as part of the normal
municipal service.
Electrical Services Report
(CVW Electrical, 2014)
The following input was obtained through the Electrical Services Report
(Annexure G4):
Mossel Bay Municipality will be the supply authority.
The supply will be provided from the newly built 66/11 kV 20 MVA
substation approximately 1km to the east of the proposed
development. The existing 11 kV network will be extended to the
west with minor upgrades required at Sonskynvallei Substation.
Each Erf boundary will be provided with 40A single-phase
electricity.
Distribution on the property (Erf) will be an 11000/420 V
underground cable system, which will have no visual impact on the
environment.
To minimise load shedding and blackouts, it is recommended that
the Municipality install energy efficient street lighting, 57 W
Compact Fluorescent‟s on 5, 4m Poles.
Heritage Report
(De Kock, 2014)
No historic structures, ruins or possible gravesites were identified
during field work. No significant structures and/or cultural
landscape patterns could be identified through early aerial imagery.
It is recommended that a focussed Integrated Heritage Impact
Assessment be undertaken which must include specialist input in
the form of an Archaeological Impact Assessment. See Annexure
G5.
Traffic Impact Assessment
(Maart, 2014)
Mandela Street will be chosen as a single access point to the
development and should be improved by a left turning lane on the
eastern approach with a minimum length of 30m.
The Gumpiro Avenue access point onto TR 33/2 to the West of
Mandela Street should be closed off. A request to formalise this
access point was raised by the Ward Committee members during a
meeting that took place on 2 July 2014 at the Sonskynvallei
Community Centre regarding the proposed development. It is
believed that the safety of the access point can be increased
significantly if the vegetation inside the road reserve is cleared.
The existing pedestrian walkway from Hartenbos to the TR 33/1 -
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Waboom Street junction needs to be extended up to the Mandela
Street access to the Sonskyn Valley development. The walkway
will be ± 950m long and should be at least 2m wide and to the
same standard as the existing facility.
An internal pedestrian walkway network should also be
implemented along Gumpiro Avenue and along the 13m wide road
reserve-roads. These walkways should be at least on one side of
the street and be a minimum of 1.5m wide.
Public transport embayments will be positioned along the 13m
wide road reserve – roads with the objective for commuters not to
walk more than 500m to the pick-up or drop-off point
See Annexure G6.
Visual Impact
Statement
(Stead, 2014)
The Visual Impact Statement indicated that the proposed development
does not constitute a significant visual impact. The viewshed analysis
indicated that the visibility of the proposed project alternatives would be
contained mainly to the foreground/midground areas (up to 6km) due to the
hilly terrain of the surrounding areas. It was found that the areas have a
high visual absorption capacity due to the strong precedent for industrial
and residential development with associated infrastructure that is already
present in the area. It is likely that the zone of visual influence will be
restricted to the high exposure areas within the 2km buffer distance.
Further detailed visual assessment is not necessary for the following
reasons:
The moderate extent of the viewshed of the proposed project
which spreads into the surrounding areas with a higher VAC level;
The proposed project‟s close proximity to the existing Sonskyn
Vallei residential development;
The alignment of the proposed project within the urban edge and
with municipal planning; and
The protection of the hill landscape via open space zoning
Stead (2014) make the following recommendations to assist in reducing the
visual intrusion effects of the proposed development:
Reduce skyline intrusion by remove units 18 – 27 off the prominent
ridgeline, as seen from the R328 road receptors (alternative 2
complies with this recommendation);
Utilization of the semi-detached dwelling option so as to reduce the
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visual footprint of development and create an appearance of more
open space (alternative 2 complies with this recommendation);
The dwellings should be painted in a grey-green colour range to
reduce visual intrusion as seen from the N2 and Hartenbos
Heuwels residential areas;
Dust control measures should be implemented during construction;
Indigenous and endemic trees should be incorporated into the
street design;
Overhead mast lighting should not be utilised; and
Street lighting should be downward directional.
See Annexure G7.
7. IMPACT SUMMARY
Please provide a summary of all the above impacts.
The change in character of the area from an undeveloped portion of land to an urban township
is LOW negative considering that the property falls within the urban edge of Mossel Bay,
which renders the change acceptable.
Figure 34: Urban Edge of Mossel Bay indicated by the blue dotted line. From the image it is clear that the existing Sonskynvallei Township as well as the proposed new development area (except for a portion of the new bulk water pipeline) falls within the urban edge of Mossel Bay (Mossel Bay SDF, 2008).
The loss of biodiversity associated with the clearing of vegetation and the transformation of
portions of the site for housing development is considered low/medium negative. The reason
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for this impact rating is due to the land currently being undeveloped and containing remnants
of natural vegetation. Conservation worthy thicket patches identified as part of the Botanical
Impact Assessment was however excluded from the development area. It also has to be noted
that provision has been made for large areas of Public Open Space along the southern side of
the proposed development area where the natural vegetation can be conserved.
Impact on Heritage resources are considered to be negligible due to the absence of old
structures/buildings or gravesites on the development site.
From an archaeological point of view the proposed development will have no impact on
significant archaeological resources and the correct manner for dealing with archaeological
resources exposed during construction is laid out in the Archaeological Impact Assessment.
Impacts on archaeological resources are considered negligible.
The proposed new development will result in an increase in traffic volumes of the area. This is
considered to be negligible as the Traffic Impact Assessment make recommendations for
best traffic management. Traffic impact is also unavoidable in terms of township development,
thus mitigation measures needs to be as effective as possible.
Providing housing in the Mossel Bay/Sonskynvallei area where there is a known housing need
is considered very high positive.
The visual impact of the proposed development does not constitute a significant impact.
The potential of increasing crime and security risks within the established township area is
considered medium negative.
No noise impacts are expected for the operation phase.
Potential erosion during construction phase is considered low negative. By following
mitigation and control measures as indicated in the Environmental Management Programme
this impact can be brought down to very low-negligible.
8. OTHER MANAGEMENT, MITIGATION AND MONITORING MEASURES
(a) Over and above the mitigation measures described in Section 6 above, please indicate any additional management, mitigation and monitoring measures.
The Mossel Bay Municipality must, as far possible, enforce a „local first‟ policy when it comes
to awarding contract for implementation of the project.
The Mossel Bay Municipality, in cooperation with the SAPS and local communities, must
attend to the challenges of crime, police response time to crime reports and consider the
establishment of a Neighbourhood Watch system that will benefit the community as a whole.
The Municipality must clear the Public Open Space areas south of the proposed development
footprint of invasive alien plants like Acacia cyclops (rooikrans).
Environmental Education boards can be put up at the Sonskynvallei Community Hall to inform
the local community of the importance of conserving the natural area surrounding them.
Boards should typically contain information regarding to littering, damage to plants and
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animals, wise water use and pollution, as well as ways to recycle household material.
The thicket patch near the rugby field which was excluded from the development must be
monitored for invasive alien plant invasion, plant harvesting and vandalism. (b) Describe the ability of the applicant to implement the management, mitigation and monitoring measures.
It is highly likely that the Mossel Bay Municipality will be able to enforce a „local first‟ policy
when it comes to awarding contracts for implementation of the project.
The Municipality‟s resources will determine whether they can implement an alien clearing
programme on the areas indicated for Public Open Space.
It is anticipated that the applicant will be able to implement the mitigation measures proposed.
It is recommended that all mitigation measures and construction activities are overseen by the
ECO to ensure minimal impact on the environment.
Please note: A draft ENVIRONMENTAL MANAGEMENT PROGRAMME must be attached this report as Appendix H.
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SECTION G: ASSESSMENT METHODOLOGIES AND CRITERIA, GAPS IN KNOWLEDGE, UNDERLAYING
ASSUMPTIONS AND UNCERTAINTIES (a) Please describe adequacy of the assessment methods used.
Assessment measures used includes:
Site visits to determine the nature and sensitivity of the land
Consultation with stakeholders
This assessment has taken into account various specialist input and recommendations,
namely: Botanical, Civil Engineering, Electrical Engineering, Heritage & Traffic Impact
Assessment.
Consideration of applicable Legislation, Guideline and Policies
The assessment methods used are anticipated to be adequate for the nature of the application and
site.
(b) Please describe the assessment criteria used.
Nature of the impact: impacts associated with the proposed housing development have been
described in terms of whether they are negative or positive and to what extent.
Duration of impacts: Impact were assessed in terms of their anticipated duration:
- Short term (e.g. during the construction phase)
- Medium term (e.g. during part or all of the operational phase)
- Long term (e.g. beyond the operational phase, but not permanently)
- Permanent (e.g. where the impact is for all intents and purposes irreversible)
- Discontinuous or intermittent (e.g. where the impact may only occur during specific climatic
conditions or during a particular season of the year)
Intensity or magnitude: The size of the impact (if positive) or its severity (if negative)
- Low, where biodiversity is negligibly affected or where the impact is so low that the remedial
action is not required;
- Medium, where biodiversity pattern, process and/or ecosystem services are altered, but not
severely affected, and the impact can be remedied successfully; and
- High, where patter, process and/or ecosystem services would be substantially (i.e. to a very
large degree) affected. If a negative impact, could lead to irreplaceable loss of biodiversity
and/or unacceptable consequences for human wellbeing.
Probability: Should describe the likelihood of the impact actually occurring indicated as:
- Improbable, where the possibility of the impact is very low either because of design or historic
experience;
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- Probable, where there is a distinct possibility that the impact will occur;
- Highly probable, where it is most likely that the impact will occur; or
- Definite, where the impact will occur regardless of any prevention measures.
Significance: The significance of impacts can be determined through a synthesis of the assessment
criteria. Significance can be described as:
- Low, where it would have negligible effect on biodiversity, and on the decision;
- Medium, where it would have a moderate effect on biodiversity, and should influence the
decision;
- High, where it would have, or there would be a high risk of, a large effect on biodiversity.
These impacts should have a major influence on the decision;
- Very high, where it would have, or there would be a high risk of, an irreversible negative
impact on biodiversity and irreplaceable loss of natural capital or a major positive effect.
Impacts of very high significance should be a central factor in decision-making.
Confidence: The level of confidence in predicting the impact can be described as:
- Low, where there is little confidence in the prediction, due to inherent uncertainty about the
likely response of the receiving ecosystem, or inadequate information;
- Medium, where there is a moderate level of confidence in the prediction, or
- High, where the impact can be predicted with a high level of confidence
(c) Please describe the gaps in knowledge.
The consulting of various specialists in the compilation of this assessment report has shown that there
are no gaps in knowledge and that informed recommendations are being made.
(d) Please describe the underlying assumptions.
It is assumed that the information that this assessment is based upon is accurate, correct and truthful
(project information).
It is also assumed that the proposed mitigation measures and Environmental Management Plan and
mitigation measures will be followed during construction and operation.
(e) Please describe the uncertainties.
No uncertainties were highlighted during the compilation of this report.
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SECTION H: RECOMMENDATION OF THE EAP In my view (EAP), the information contained in this application form and the documentation attached hereto is sufficient to make a decision in respect of the activity applied for. YES NO
If “NO”, list the aspects that should be further assessed through additional specialist input/assessment or whether this application must be subjected to a Scoping & EIR process before a decision can be made: If “YES”, please indicate below whether in your opinion the activity should or should not be authorised: Activity should be authorised: YES NO Please provide reasons for your opinion
The proposed development site falls within the urban edge of Mossel Bay, therefore the
proposal for township development is in line with forward spatial planning of the area.
The site is very well located, in that is accessible via the existing roads. Furthermore,
although the proposed development includes community facilities (i.e. church, crèche, and
business erven) it is located adjacent to existing facilities like the sport fields, community
centre and clinic.
There is a need for housing in the Sonskynvallei area and it is the responsibility of the
Mossel Bay Municipality to provide housing opportunities to local communities.
The Mossel Bay Municipality‟s intent to provide housing forms part of the National Strategy
for housing.
The Municipality has confirmed that with the recommended upgrades (bulk water pipeline)
there will be sufficient capacity within the system to service the proposed development in
terms of water (sewage and drinking), electricity and refuse removal – Annexure E2 & E3.
The development proposal has been informed by various specialist assessments.
The thicket patches around the rugby field as well as along the north-western boundary of
the development area has been avoided as per recommendation of the specialist – reflected
in preferred layout alternative 2.
The NFEPA area which is considered to be sensitive will be avoided by realigning the new
water pipeline along the existing gravel track that runs to the existing reservoir.
The impacts of the proposed housing development on archaeological resources are
considered negligible.
Semi-detached houses, as per specialist recommendation, will have less visual impact as it
will create the impression of larger open space areas. Other visual recommendations will also
decrease the already insignificant visual impact.
The proposed development is in-line with the character of the area which consist of
Sonskynvallei Phase 1 as well as the approved Phase 2 of Sonskynvallei.
The proposed mitigation measures as well as the Environmental Management Programme
will inform sound environmental monitoring and management practices for the duration of the
construction phase as well as operational phase.
Although the proposed development will result in loss of undeveloped land, it is outweighed by
the benefits of providing housing opportunities in an area where there is a housing need.
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The development layout has made provision for fairly large areas of Public Open Space
south of where the proposed housing opportunities are to be constructed.
If you are of the opinion that the activity should be authorised, then please provide any conditions, including mitigation measures that should in your view be considered for inclusion in an authorisation.
An Environmental Control Officer (ECO) should be appointed prior to construction to
facilitate induction of the contractor‟s team, and to oversee the construction period.
The ECO must ensure that construction activities remain within the guidelines set out in the
Environmental Management Programme as to ensure no negative impacts on the
environment.
Solid waste and any waste generated from construction activities must be disposed of at a
recognised site and in the correct manner.
Water saving measures described in the EMP must be followed.
It is recommended that the thicket patches excluded from the development footprint be
regularly monitored for invasive alien plant invasion and damage/vandalism.
Ensure that landscaping will only use natural, preferably indigenous, vegetation.
Fynbos is a fire driven system and it is recommended that the Municipality implement and
maintain proper fire breaks along the edges of the township to avoid unnecessary damages
to property or livelihoods.
Duration and Validity: Environmental authorisations are usually granted for a period of three years from the date of issue. Should a longer period be required, the applicant/EAP is requested to provide a detailed motivation on what the period of validity should be. Implementation of the project is subject to various funding application processes between the Mossel
Bay Municipality and the Provincial Department of Human Settlements. Successful applications will
unlock funding for the implementation of this project. Since the time period for such processes is
unknown it is recommended that a period of no less than five (5) years be considered for the period of
validity of the Environmental Authorisation.
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SECTION I: APPENDICES The following appendices must be attached to this report:
Appendix Tick the box if Appendix is attached
Appendix A: Locality map X
Appendix B: Site plan(s) X
Appendix C: Photographs X
Appendix D: Biodiversity overlay map X
Appendix E: Permit(s) / license(s) from any other organ of state including service letters from the municipality X
Appendix F:
Public participation information: including a copy of the register of interested and affected parties, the comments and responses report, proof of notices, advertisements and any other public participation information as required in Section C above.
X
Appendix G: Specialist Report(s) X
Appendix H : Environmental Management Programme X
Appendix I: Additional information related to the Application – Background Information Document (BID) X
Appendix J: Any Other (if applicable) (describe) N/A
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