Environmental Management Programme for Climbing on the Peninsula Mountain Chain:
March 2000

TABLE OF CONTENTS
CHAPTER 1: INTRODUCTION
1.1 1.1 Background To Climbing On The Peninsula
1.2 Approach to the Environmental Management Plan
1.3 Scope of this Document
CHAPTER 2: ENVIRONMENTAL POLICY
CHAPTER 3: ENVIRONMENTAL IMPACTS AND ISSUES
3.1 Potential Impacts Identified
3.2 Significance Of Impacts
CHAPTER 4: MANAGEMENT PLAN
4.1 Organisational Structures
4.2 Proposed Categories Of Climbing Venues
4.3 Management Objectives And Actions
4.4 Management Of New Routes And Venues
4.4.1 Existing Sport Climbing Venues
4.4.2 Sport Climbing Venues in Sensitive Areas
4.4.3 New Proposed Sport Climbing Venues
CHAPTER 5: IMPLEMENTATION AND REVIEW
5.1 Responsibilities And Monitoring
5.1.1 South African National Parks
5.1.2 Sport Climbing Working Committee
5.2 Correction And Enforcement
5.3 Review
CHAPTER 6: List of Contributors and References
6.1 Contributers
6.2 Consultation with Sport Climbers
6.3 Way Forward
6.4 References

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Environmental Management Programme for Climbing on the Peninsula Mountain Chain


Draft proposal - March 2000

CHAPTER 1: INTRODUCTION

1.1 Background To Climbing On The Peninsula

The first recorded ascent of Table Mountain was in 1488 by Antonia de Saldanha. The first rock-climbs were, however, only established many years later by Jim Searle between 1894 and 1895. Rock-climbing developed very rapidly after this especially with the achievements of George Traverse-Jackson between 1895 and 1907 and later by Berrisford, Londt, Marcus, Kaplan, Cameron, Mamacos, Fletcher, Scott and others. In the 100 years of rock-climbing on the Cape Peninsula since 1894 when Searle first climbed Right Face, climbing development has been closely aligned to new developments in equipment.

The initial routes of Searle and Traverse-Jackson were climbed without the benefit of any safety precautions such as ropes or belays. Around 1914, with the introduction of rubber-soled shoes, climbing grades shot up dramatically and by the 1930's the leader passed the rope over projections in the rock face as a safety precaution in the event of a fall. The golden rule, however, was that the leader never fell because the hemp rope running over a rock belay would in all probability snap if shock loaded. After World War II, due to the technological advances of the War, nylon ropes and slings as well as pitons and karabiners became available. With these advances in equipment came major advances in safety and as leader safety improved so too did the standard of climbing. The Journals of the Mountain Club of South Africa record the controversies that arose with every advance in equipment, but these same Journals also record the major advances in rock-climbing made by this technology. By the mid 1970's the piton had been totally replaced by metal wedges which could be placed or removed by hand, ropes were cheaper and more easily available and leaders now fell more readily.

It is at this stage that climbing grades on the Peninsula reached a peak. With all the improvements in gear through the 1980's especially in footwear, the grades of the new routes did not increase dramatically until a new trend of short (10-20m) routes started to develop. This trend pushed the standard of climbing on the Peninsula to an all time high. New routes were still, however, restricted to cracks and other natural faults in the rock in which protection for the leader could be inserted.

Through the 1980's and starting on Lions Head fixed protection in the form of bolts began to make an appearance. This form of protection now made accessible rock that would otherwise be unsafe due to a lack of natural features for protection and enabled climbers to do harder routes. Termed 'Sport Climbing', this new development in safety has meant a massive increase in the popularity of climbing. For the first time, the leader could fall with relative impunity.

This increase in safety has meant that there are now more people climbing on the Peninsula than ever before. The Cape Peninsula has a high concentration of fully equipped sport routes and is an exceptionally valuable resource for climbers, as the mountains are easily accessible and offer a very high quality of route. The resource is not limitless, however and the ever increasing popularity of sport climbing will impact on it. It is now more imperative than ever that climbing is properly managed. This document is the first step in that direction.

1.2 Approach to the Environmental Management Programme

The Environmental Management Programme proposed in this document is broadly based on the ideas outlined in the ISO 14000 Specifications for Environmental Management Systems (EMS) (SABS, 1996). An EMS can provide an orderly and consistent approach to addressing climbing related environmental issues. It does not establish absolute requirements for environmental performance, however, it does provide an outline of the process and elements needed for an effective system to manage impacts.

The Environmental Management Plan outlined in this document involves an ongoing process of formulation, planning, implementation and evaluation of an environmental policy. The steps required in this process are outlined below:

* Environmental Policy
The environmental policy forms a statement of climbers intentions regarding their environmental performance. It provides guiding principles and aids in the setting of objectives and targets. This policy needs to be endorsed by climbers.

* Planning
The activities relating to sport climbing have been reviewed and an initial assessment has established the impact they have on the environment. This provides a starting point from which objectives and targets for management can be set. The degree of practical control over the environmental aspects being considered should be taken into account. Priority objectives and targets need to be decided upon and a management programme and tools developed to meet them. Resources are also committed for implementation. Part of this programme has been developed for comment but it needs to be endorsed by climbers and SANP.

* Implementation
This requires the execution and operation of the management programme.

* Review and evaluation leading to improvement
Deficiencies and shortcomings in the management plan will need to be addressed and the effectiveness of the programme checked. It is important that the EMS is continually reviewed and improved with the objective of improving overall environmental performance.

An Environmental Management Plan based on the principles of EMS thus forms a flexible system that is adaptable to changing circumstances.

1.3 Scope of this Document

Subject to the approval of South African National Parks (SANP), this document sets out a number of proposals to manage sport climbing and bouldering on the Peninsula Mountain Chain

This document sets out the beginnings of a proposed management system for climbing on the Peninsula. An environmental policy has been formulated which clearly outlines the principles by which climbing activities will be guided.

The potential impacts of climbing have been identified and an initial assessment undertaken.

After discussions held at the Upper Cable Station on Table Mountain with South African National Parks representatives in 1997 it was decided that traditional (adventure) climbing and scrambling would not be included in this document because of the limited environemental impacts associated with this type of climbing. However, despite this decision, all climbers should be committed to the environmental concerns inherent in Chapter Two and Chapter Three of this document

A draft management programme has been proposed that outlines how a Sport Climbing Working Committee (SCWC) together with climbers will monitor and regulate sport climbing activities and the impacts associated with this form of climbing. This system will hopefully enable the SCWC to work jointly with SANP o maximise the benefits of climbing whilst minimising the negative environmental impacts. The proposals set out in this document should form the basis for an ongoing and growing system to manage sport climbing on the Peninsula. NOTE: While this document intends for the regulation of the sport, climbing is an inherently dangerous sport and prospective climbers must recognise that the responsibility for their safety lies purely with themselves.

CHAPTER 2: ENVIRONMENTAL POLICY

Climbers are committed to minimising the adverse effects of their activities on the environment and to promote the safe practice of the sport. To this end they are committed to the following principles:

* Minimising the impact of climbing activities on the natural environment, including indigenous fauna and flora
* Minimising the visual impact of fixed protection
* Minimising impacts on the cultural and historical environment includig all archaelogical and palaeontological sites
* Adhering to standards for fixed protection that conform with safety standards appropriate to environmental conditions on the Cape Peninsula
* Co-operating with managing authorities and recognising and responding to their concerns
* Identifying and assessing the significance of impacts associated with potential new climbing areas in conjunction with SANP and other interested and affected parties
* Monitoring sport climbing and bouldering activities to ensure compliance with the principles outlined above

This environmental policy provides a framework for action and the setting of objectives and targets.

CHAPTER 3: ENVIRONMENTAL IMPACTS AND ISSUES

This section provides an overview of the potential environmental impacts of climbing and their significance. This provides a starting point from which the objectives and targets for management can be set.

3.1 Potential Impacts Identified

The potential impacts that have been identified in relation to activities associated with climbing are presented in Table 1. The status of these potential impacts is also indicated i.e. whether they are positive (+ve) or negative (-ve).

Table 1. The potential impacts of climbing
Activities Potential Impacts Status
Walking to and from venue Erosion of footpaths
Trampling and removal of indigenous vegetation
Litter
Access to natural environment
Exercise
Awareness of environmental issues
-ve
-ve
-ve
+ve
+ve
+ve
Belaying and Climbing Erosion of base of crag
Trampling of indigenous vegetation
Removal of indigenous vegetation
Disturbance of animals and nesting/ endangered birds
Litter
Waste
Disturbance of archaeologically sensitive sites
Trampling and removal of alien vegetation
Recreational use of the natural environment
Positive psychological experience
Physical exercise
-ve
-ve
-ve
-ve
-ve
-ve
-ve
+ve
+ve
+ve
+ve
Bolting/New routes/Retrobolting Removal of indigenous vegetation
Disturbance of animals and nesting/endangered birds
Visual impact of fixed protection
Damage to rock art
Noise from drilling
Increased tourism
Climbing/Leading and lower-off safety
Positive psychological experience
-ve
-ve
-ve
-ve
-ve
+ve
+ve
+ve

3.2 Significance Of Impacts

A significance rating has been determined for the potential impacts that have been identified. The criteria used to determine the significance ratings are presented in Table 2 and the significance of the potential impacts are outlined in Table 3.

Table 2. Criteria used to determine the significance ratings
Criteria Categories
Spatial extent/influence of impact Site specific or local
Regional
National
Magnitude of impact at spatial scale
High: Natural and/or social functions and/or processes are severely altered
Medium: Natural and/or social functions and/or processes are notable altered
Low: Natural and/or social functions and/or processes are negligibly altered
Duration Temporary (<1 year)
Short term (1 to 6 years)
Medium term (6 to 10 years)
Long term (> 10 years)

Given these criteria, the significance ratings have been defined as below:
* High: impacts of high magnitude locally for longer than 6 years and/or regionally and beyond
* Medium: impacts of moderate magnitude locally to regionally in the short term
* Low to very low: impacts will be localised and temporary.
* No impact: a potential concern or impact which, upon evaluation, is found to have no significant impact at all.

It should be noted that for some of the potential impacts that were identified, their significance may vary from area to area. This will depend on the specific conditions present at a particular climbing venue. For example, erosion at the base of a climbing area will depend on how susceptible the soil is to erosion and the amount of solid rock present. In Table 3, the significance ratings have been assigned for impacts both without and with management actions.

Table 3: Significance of Impacts
Activities Potential Impacts Status Significance: No management Significance: Management
Walking to and from venue Erosion of footpaths
Trampling and removal of indigenous vegetation
Litter
Access to natural environment
Exercise
Awareness of environmental issues
-ve
-ve
-ve
+ve
+ve
+ve
High
High
Medium
Medium
Low
Medium
Low
Medium
No impact
Medium
Low
Medium
Belaying and Climbing Erosion of base of crag
Trampling of indigenous vegetation
Removal of indigenous vegetation
Disturbance of animals and nesting/endangered birds
Litter
Waste
Disturbance of archaeologically sensitive sites
Recreational use of the natural environment
Positive psychological experience
Physical exercise
-ve
-ve
-ve
-ve
-ve
-ve
-ve
+ve
+ve
+ve
High
Medium
High
Medium
Medium
Low
High
Medium
Medium
Medium
Low
Low
Medium
Low
Low to No impact
Low to No impact
Low to No impact
Medium
High
Medium
Bolting/New routes Removal of indigenous vegetation
Disturbance of animals and nesting/endangered birds
Visual impact of fixed protection
Damage to rock art
Noise from drilling
Increased tourism
Climbing/Leading and lower off safety
Positive psychological experience
-ve
-ve
-ve
-ve
-ve
+ve
+ve
+ve
High
Medium
Medium
High
Low
Medium
Medium
Medium
Medium
Low
Low
Medium
Low to No impact
High
High
High

CHAPTER 4: MANAGEMENT PLAN

This section sets out a proposed management plan to regulate climbing, new routes and manage impacts.

4.1 Organisational Structures

The environmental management plan will involve different organisations and groups of people. These are described below and the roles and responsibilities of these various structures is detailed further in the management programme

* South African National Parks (SANP)
South African National Parks (SANP) are the managing authority of the Cape Peninsula National Park and as such, are the ultimate decision making authority. They have the right to establish rules and regulations regarding all activities within the national park.

* Sport Climbing Working Committee
It is proposed that a Sport Climbing Working Committee (SCWC) that consists of representatives from the climbing community, be democratically elected by climbing users of the Peninsula Mountain Chain. The committee should consist of no less than 5 members. There should be continuity from one elected committee to the next, in that two members of each committee should serve a double term. Election of members will take place at a meeting called specifically for the purpose and votes will also be accepted by proxy, e-mail, letter or fax.

The first committee elected will be responsible for drawing up a constitution. This committee will set in place clear criteria and guidelines for dispute resolution.

4.2 Proposed Categories Of Climbing Venues

In order to manage the impacts detailed in Section 3, it is proposed that four different categories of venue be created which will be subject to differing levels of control in respect of management and approval of new sport routes. Procedures for management and application for new sport routes in each of the proposed types of venue are listed.

The following categories of venue are suggested in order to facilitate their management:

* Existing sport climbing venues
These are areas that currently have sport routes, and are widely utilised. In most cases, access has been negotiated and granted, and in some instances use of the venue is implicit (such as the use of quarries).

* Sport climbing venues in sensitive areas
These are areas that currently have sport routes and are widely utilised for this purpose. Certain conditions have made some portion or all of these venues sensitive enough to require a higher level of management

* New proposed sport climbing venues
Other opportunities exist for new venues. Such new venues will require an environmental assessment before use is granted. If a venue is approved it will be delegated into one of the aforementioned two categories.

* Bouldering areas
These areas consist of groupings of boulders where bouldering is done.

Annexure 1 provides a map of the Cape Peninsula showing present sport climbing venues, and Annexure 2 shows envisaged categorisation of these venues. All climbing venues presently utilisd forsport climbing will have to be assessed and approved at the implementation of the management programme.

4.3 Management Objectives And Actions

A bi-annual meeting is proposed between the SCWC and SANP to discuss the status of management of climbing activities on the Peninsula. In addition, a number of management objectives and actions are outlined below. These management actions are to apply to all climbing venues. All climbers will be expected to comply with the provisions outlined below.

Many of the management actions discussed below should occur on self-regulatory basis, with climbers taking responsibility for their own actions. These management actions are to be taken in respect of all types of climbing venue being used i.e. existing venues, venues in sensitive areas.

* Erosion
The SCWC will monitor the state of paths and discuss this at a proposed bi-annual meeting between the SCWC and SANP. A summary report (inclduing maps where necessary) detailing actions needed to upgrade paths should be drawn up before the meeting. The total number of new paths required to service new venues is probably minimal and some existing paths are urgently in need of maintenance.