Richard M. Cowling2
Brian W. van Wilgen3
1South African National Parks, Scientific Services: Garden Route, Sedgefield, South Africa
2Department of Botany, Nelson Mandela Metropolitan University, Port Elizabeth, South Africa
3Centre for Invasion Biology, CSIR Natural Resources and the Environment, Stellenbosch, South Africa
PO Box 176, Sedgefield 6573, South Africa
Received: 18 Feb. 2011
Accepted: 03 May 2011
Published: 12 Sept. 2011
How to cite this article:
Kraaij T, Cowling RM, Van Wilgen BW. Past approaches and future challenges to the management of fire and invasive alien plants in the new Garden
Route National Park. S Afr J Sci. 2011;107(9/10), Art. #633, 11 pages.
© 2011. The Authors. Licensee: AOSIS OpenJournals. This work is licensed under the Creative Commons Attribution License.
ISSN: 0038-2353 (print)
ISSN: 1996-7489 (online)
Past approaches and future challenges to the management of fire and invasive alien plants in the new Garden Route National Park
In This Review Article...
• The Garden Route mountain catchments
• Biophysical environment
• Institutional context
• History of catchment and fire management
• Management challenges
• Fire management
• Historical legacy
• Sustainable management at landscape scale
• Way forward
• Research priorities
• Management interventions to be considered
• Fire management
• Invasive plant control
• Landscape rationalisation
The recently established Garden Route National Park (GRNP) along the Cape south coast of South Africa occurs in a landscape where indigenous forests,
fire-prone fynbos shrublands and fire-sensitive plantations of alien invasive trees are interspersed. We used the area as a case study in the challenges
facing conservation managers in the achievement of biodiversity goals in a fire-prone environment. We explored the context within which fire management
was practised during the past century by interviewing former catchment managers and reviewing forestry and catchment management policies. Mountain fynbos
adjacent to plantations was subjected to burning regimes aimed at the protection of commercial timber resources rather than the preservation of fynbos
biodiversity. Prescribed burning of fynbos adjacent to the plantations was typically done in multiple belt systems at rotations of about 4–8 years
during spring, summer and autumn, to avoid the winter berg wind season. Such short-rotation and low-intensity fires favour resprouting graminoids over
slow-maturing reseeders, and likely account for the compositional impoverishment observed in fynbos near plantations. Current and future challenges faced
by the GRNP include (1) balancing conflicting fire management requirements for plantation safety against fynbos conservation; (2) the continual
invasion of fynbos by fire-propagated alien pines sourced from plantations; (3) inadequate resources to redress the ‘invasion debt’ caused
by the socio-economic legacy and past management neglect; and (4) fragmentation of land use between conservation and forestry threatening the sustainability
of the region at large. We provide recommendations for management actions and research priorities to address these challenges.
Fire has been a key process and evolutionary force shaping plant traits and vegetation communities across the globe for much of its
history.1,2 It has been the most ubiquitous terrestrial disturbance, surpassed more recently only by human transformation
of the landscape.3 Anthropogenic changes in land use have in turn resulted in modifications in the way fire occurs in space
and time,1 along with changes in our perceptions of fire and demands placed on land management agencies to protect lives and
In the exceptionally diverse7 and threatened8 Mediterranean-climate (summer drought, winter rain) biotas of the world,9
fire is the most important ecological disturbance factor and predates humans in these ecosystems.2,10 Mediterranean floras have evolved
specialised post-fire persistence traits, which are sensitive to the specifics of fire regimes, such as seed banking in the soil or canopy, resprouting,
and fire-stimulated flowering and germination.9,11 Fire is instrumental in maintaining diversity in the fynbos of the Cape Floral Kingdom (CFK)
of South Africa,12 and may be considered the most important fynbos management practice, being both a key ecological factor and a practical tool
for resource manipulation.
The fire ecology of fynbos has been well researched since the early 1970s and by the 1990s fairly detailed fire management prescriptions were
available.13,14,15 However, much emphasis was on the western, strictly winter-rainfall part of the
CFK12,16 and the inland arid mountains,17,18,19 whereas the eastern coastal part of the CFK has been neglected. The
climate of the eastern coastal part is less seasonal (rainfall is bimodal20,21) and species’ phenology,22
and possibly plant growth and maturation rates, differ accordingly, which has implications for the management of fire regimes.
Fuel-reduction burning in fynbos (as in south-eastern Australia23) largely developed from the early 1900s in response to the need to
protect commercial timber resources. Early fire legislation has hence been embedded in forestry acts.24,25 Fire management
practices aimed at hazard reduction are often in conflict with ecological objectives.6,23 Simple management compromises
intended to reconcile conflicting objectives may ultimately not achieve either hazard reduction or biodiversity conservation.23
Therefore, management agencies have to set very clear and realistic objectives to determine the most appropriate management practices for each
particular area.24,26 In the fynbos, as elsewhere, invasion by fire-adapted plants can complicate fire management. Invasion of fynbos
ecosystems by invasive trees and shrubs, and notably by pines, is one of the largest threats to conservation.15 These invasive pines
originate from commercial plantations that have been established throughout the CFK, and they often exacerbate the potential negative effects of
both altered fire regimes and invasive species.1,10,15
Improved understanding of fire ecology is becoming increasingly important as climates change, protected area networks expand, pressure from alien
invasive biota increases, the wildland–urban interface enlarges, and demands to manage fuel loads of natural habitat for asset protection
grow.4,15,27,28 Where new protected areas are established, systems are likely to be poorly
researched and management prescriptions may have to be made in the absence of a clear understanding of ecosystem processes and responses. Recent
additions to protected areas are often not in pristine condition and are affected by historic management that has implications for management into the future.
The recent establishment of the Garden Route National Park (GRNP; ~130 000 ha29) along the Cape south coast of South Africa
involved the amalgamation of certain parcels of land. These land parcels have in the past been variously managed for water conservation, biodiversity
conservation, plantation forestry using alien invasive species, and the harvesting of natural resources, mainly timber from indigenous forests.30
We used the fynbos areas of the GRNP as a case study for exploring the challenges facing conservation managers in the achievement of biodiversity goals in
a fire-prone environment. Our analysis was underpinned by a number of issues. Firstly, the GRNP is located within the south-eastern coastal part of the CFK
where fynbos fire ecology is inadequately understood. Secondly, it is a new park, and a reconstruction and critical review of past fire management
approaches is needed. Thirdly, the institutional history and landscape context of the park pose particular difficulties that need to be addressed by the
fire management policy, including high levels of invasion by alien trees, and significant pressure from the adjacent plantation industry to reduce wildfire
hazard. Being a new park, there is still opportunity to influence the management policy and practice in the interest of biodiversity conservation.
In this paper we present the environmental and institutional context within which historical catchment management practices in the region of the GRNP evolved,
and we consider how the adoption of a new mandate, with conservation as its central goal, will require changes to research priorities, management actions and
The study area is broadly defined as the southern slopes of the Outeniqua Mountains east of the Touw River, and the southern slopes of the Tsitsikamma
Mountains (22.59°E – 24.26°E; hereafter collectively referred to as the Garden Route coastal mountains, GRCMs), with emphasis on those
areas recently proclaimed as part of the GRNP29 (Figure 1). The GRCMs form part of the Cape Fold Belt Mountains31 and run in an
east–west direction, parallel to the coast.32 The highest peaks in the eastern Outeniqua and Tsitsikamma Mountains are 1469 m and
1675 m, respectively. Deeply incised remnants of an early Cenozoic peneplain form the coastal foreland south of these mountains.32 The
Table Mountain Group rocks of the Cape Supergroup are the main mountain-forming substrata.31 Acidic (pH 3.3 – pH 5.5)
lithosol soils, which are moderately deep, dark-coloured loamy sands, generally poor in bases, phosphorus and nitrogen, predominate.33,34
FIGURE 1: Map of the study area showing the distribution of fynbos, indigenous forest and decommissioning plantations (to be clearfelled and rehabilitated) within
the boundaries of the Garden Route National Park (GRNP). The shown distribution of remaining plantations, on state land and managed by Mountain to Ocean
Forestry, follows the recommendations for the partial reversal of the plantation decommissioning strategy. The map is split into (a) the Outeniqua region and (b) the
Owing to maritime influence, the climate of the GRCMs is relatively temperate. In contrast to the strictly Mediterranean climate in the western part of the
CFK, rain falls throughout the year.21,22 Rainfall peaks in spring and autumn, winter months are the driest, and the proportion of summer rain
increases eastwards.35 Annual rainfall increases eastwards, the mean for the Outeniqua and Tsitsikamma Mountains being 820 mm and 1078 mm,
respectively.34,36 Rain is mostly cyclonic and orographic with occasional thunderstorms.34 Lightning occurs throughout the year and at a
density of < 2 flashes/km2/year.32 Temperatures are mild with mean minima and maxima ranging from
7 °C and 19 °C in June to 15 °C and 26 °C in January.34,36 South-easterly winds prevail in summer and
north to north-westerly winds (hot dry berg winds) prevail in autumn and winter, whilst south-westerly winds occur throughout the year.34,36
Berg wind conditions in particular increase the fire potential19 and are associated with a higher incidence of fire, as well as an increase
in the severity and size of fires.21
The coastal slopes of the eastern Outeniquas contribute run-off to various rivers, some of which support estuarine systems of national and international
importance37 (Figure 1). The coastal slopes of the Tsitsikammas are drained by short rivers flowing through deep gorges incised through the
coastal plain.36 In 1986, the water draining from the state-managed GRCMs was estimated to be 1046 million cubic metres per annum, then
valued at R178 billion.30 Sustained yields of water from these catchments are vital to agriculture and coastal towns in the area,38
a dependency that has been highlighted by recent severe droughts.39
The vegetation of the area comprises fire-prone and fire-dependent fynbos shrublands, interspersed with lesser areas of fire-free and fire-resistant
Afrotemperate forest. The fynbos mostly occurs between the mountain crests and the belt of indigenous forest on the coastal platform at the foot slopes
of the mountains32 (Figure 1). South Outeniqua Sandstone Fynbos and Tsitsikamma Sandstone Fynbos occur to the west and east of the Keurbooms
River, respectively.33 Both these vegetation types are tall, medium-dense proteoid shrublands, with medium-tall, dense ericoid-leaved shrub
understoreys and a prominent restioid component. Ericaceous fynbos dominates at high altitudes, grassy fynbos at lower altitudes, and forest in fire
Plantations of alien pine trees (Pinus pinaster Aiton and Pinus radiata D.Don) have fragmented and replaced large tracts of fynbos, mostly along
the lower and mid-mountain slopes (Figure 1). The plantations of Bergplaas, Karatara and Buffelsnek in the Outeniquas, and Kromrivier in the Tsitsikammas, reach
deeper into the upper catchments. The extant fynbos of the GRCMs thus typically abuts the commercial plantations to the south. Depending on the topography and
altitudinal reach of the plantations, the fynbos forms a belt of 2 km – 6 km wide, and is generally narrower along the Outeniquas than along the
Tsitsikammas (Figure 1). Considerable tracts of unprofitable plantations in the Outeniqua Mountains are in the process of being phased out, scheduled for
rehabilitation to fynbos and incorporation into the GRNP during the next decade.40,41 The landscape setting of the GRNP is thus a mosaic of fynbos
and forest amongst remaining and decommissioned plantations, most of which were formerly owned and managed by the state (the extent of these land groupings is
indicated in Table 1 and Figure 1). The mix of fynbos and fire-prone pine plantations in the landscape has led to two major management problems: (1) the need
to protect the plantations from fire, which kills the adult trees; and (2) invasions by fire-adapted pines, where fire drives the rapid spread and proliferation
of these species42 (Figure 2).
TABLE 1: Extent of Fynbos and Forest Biomes within the Garden Route National Park and the extent of former state-owned plantations, now managed by Mountain to
FIGURE 2: A landscape mosaic characteristic of the Tsitsikamma region, with
dairy pastures in the foreground, a pine plantation in the middle ground, and
mountain fynbos invaded by pine trees in the background. The lucrative dairy
industry and coastal towns in the region are dependent on water emanating
from the pine covered catchments.
Since the early 1900s, water and soil conservation have been central to the management (and acquisition in places) by the South African state of
fynbos mountain catchments, including the approach to fire management in these areas.15,24,30 However, plantation-based timber production
has from early on been recognised as a major land use and catchment management consideration in the GRCMs,30 perhaps more so than in other
fynbos catchments. The first state plantations in the area were established in 1883 near the town of Knysna.24,43 The state has since then,
until the early 1990s, actively encouraged and subsidised the industry as a strategic move to provide for the country’s demand for timber and to
alleviate pressure on the limited and over-exploited indigenous forests.43,44 Considerable expansion occurred in response to timber
shortages experienced during the First and Second World Wars. Afforestation was further promoted as a means to relieve poverty amongst unemployed
White people (1918 – 1938) and Italian prisoners of the Second World War.24,43,44 ‘Off-site planting’ resulted
from the application of poverty relief labour, whereby some of the areas planted were unsuitable for commercial plantation forestry.44 The
former Cape Province (including the present Western and Eastern Cape Provinces) was the only province where state plantations covered more area (three
times more) than private plantations.45 The state was thus the main player in the forestry industry in the Cape Province and largely focused
on growing pines.46
The generally held notion at the turn of the 19th century was that forests increase rainfall.24 Afforestation was accordingly seen as a
beneficial land use in mountain catchments which otherwise had limited economic potential.24 However, droughts, public complaints about
reductions in stream flow, and alleged desertification of South Africa during the first half of the 20th century prompted the Department of Forestry
to undertake hydrological research in mountain catchments.24,47 This research exposed the high water consumption of plantation trees,48
which led to the introduction in 1972 of an afforestation permit system to regulate new afforestation according to impacts on catchment run-off.43,49
Although it was by then recognised that afforestation competes with the conservation of water supplies and floral diversity, plantation forestry in the GRCMs
was justified because ‘surplus water [is] presently still flowing into the sea from the humid coastal mountain ranges’30.
For most of the 20th century, the state-owned mountain catchments of the Outeniquas and Tsitsikammas were managed by the national Department of Forestry (DoF)
in its various forms38,45 – either an independent department, or a branch of the national departments of Environment Affairs or Water
Affairs25,50 (for simplicity, we henceforth refer to DoF). The state managed a combination of fynbos, indigenous forests and exotic timber
plantations on state land. During the mid-1970s, DoF adopted a formal policy of ‘multiple use’, which included timber production (from both
indigenous forests and plantations), fire management and alien invasive plant control in the catchments, soil and water conservation and
recreation.24,25,30,51 The same labour force that planted and tended pine trees also cleared alien invasive plants and conducted prescribed fires.
The managers of these forestry estates were compelled to consider all aspects of this ‘multiple use’. However, governmental restructuring of DoF
during the mid-1980s, separated plantation forestry (a commercial undertaking, earmarked for privatisation), catchment fynbos and indigenous forest management
(conservation undertakings), and research.25,49,52,53 The restructuring divided the land into (1) plantations, which were transferred to the
South African Forestry Company Limited (SAFCOL); (2) fynbos areas that had not been afforested and were to be devolved to provincial nature conservation
agencies; (3) indigenous forests, which remained under the jurisdiction of DoF; and (4) research areas, which went to the Council for Scientific and Industrial
Following restructuring, large tracts of mountain fynbos within the former Cape Province were transferred to Cape Nature Conservation (which later split into
CapeNature in the Western Cape Province and Eastern Cape Parks and Tourism Agency in the Eastern Cape Province), accompanied by reductions in state funding of
conservation management functions. However, DoF retained responsibility for large areas of the state-owned catchments in the GRCMs to the north of plantations
for the purposes of fire protection.53,55 Prior to the restructuring, DoF largely achieved the fundamental principles of catchment management, that
is, nature conservation51 and sustainable water delivery, by applying appropriate fire and alien plant control regimes. With the commercialisation of
state-owned timber plantations and the establishment of SAFCOL (owned by the Department of Public Enterprises) in 1993, the focus shifted to explicitly growing
trees for profit.44,54 Nationally, privatisation of SAFCOL was largely finalised by 2002, although a buyer could not be found for the Western and
Southern Cape plantations (including the study area), packaged as Mountain to Ocean (MTO) Forestry.56 MTO Forestry was only sold to Cape Timber
Resources in 2004, based on a 70-year land-lease agreement with DoF.54,56 However, SAFCOL retained a 25% share on behalf of the government in all
privatised plantations.41 The costly burden of catchment management (and in particular fire and alien plant management), which yields no financial
return on investment, was not the primary mandate of the plantation companies. Likewise DoF, the landowner, has neglected to assume or delegate management
responsibility for those areas originally retained for the purposes of fire protection of the plantations.55 In the process, large tracts of
unafforested fynbos in the GRMCs were left without a custodian and became known as the ‘no-man’s land’.53 Management of the GRMCs
languished for almost 20 years.44 Only recently has the management of this ‘no-man’s land’ been assigned to South African National
Parks (SANParks) with the incorporation of the formerly DoF-managed forests and fynbos into the new Garden Route National Park.29,41
In 2000, the South African government decided to phase out plantation forestry in much of the Western Cape Province, including the Outeniqua region, as
these plantations were economically and environmentally unsustainable.40,41,54 Approximately 45 000 hectares of plantations (most of which
were in the Outeniqua region) were to be felled over a 20-year period and converted to other land uses.41,54,56,57 However, this decision was
partly reversed in 2006,77 with approximately half the area recommissioned for plantation forestry (Table 1; Stehle T 2010, personal communication,
November 25) on account of changing markets and the national demand for timber exceeding the growth of plantations.41 The decision was based on the
presumption that productivity of the plantations in the Outeniqua region could be substantially increased by appropriate silviculture, site-specific soil
preparation and continuous fertilisation.58
History of catchment and fire management
The general approach to fire management in fynbos mountain catchments during the 20th century is presented elsewhere.15,30 Here we
specifically focus on the approach to catchment and fire management in the GRCMs during the past century, as informed by our review of historical
policy and management documentation and interviews with past and current land managers (Table 2).
TABLE 2: Chronological account of the approach to fire management in the fynbos of the Garden Route coastal mountains (GRCMs), based on interviews with former
catchment managers and a review of catchment management policies of the national Department of Forestry (DoF).
Prescribed burning of mountain fynbos became fully accepted as a management practice during the 1970s to promote water, soil and biodiversity
conservation.30 The general approach to fire management was based on, and continually influenced by, sound ecological principles emerging
from a productive fynbos research programme at the time.14,15 However, and in contrast to policies elsewhere in the fynbos, nature conservation
was the primary objective only in parts of state catchments zoned as nature reserves. Fire protection of plantations was the primary objective in vast
areas of fynbos in the GRCMs to the north of the plantations (Table 2), where high-hazard, berg wind-driven fires characteristically originated.
For the conservation of fynbos, moderate to high-intensity fires at 10–20 year intervals are optimal.15 Conversely, for plantation protection
purposes, it is desirable to burn adjacent fynbos vegetation under cool, safe conditions as soon as there is sufficient fuel available to sustain a fire,
usually at vegetation ages of 3–8 years, depending on site characteristics. Various systems have been proposed and/or pursued in the GRCMs in an
attempt to reconcile this fundamental conflict of interest.23 The most common approach has been the so-called double- (or triple-) belt system
(Table 2). Accordingly, fynbos to the north of the plantations was divided into two to three parallel belts, each burnt at a fixed rotation, for example
every eight years but four years apart. The vegetation age in one of the belts would consequently always be four years or less, thereby reducing the likelihood
of fires spreading from catchment fynbos to the plantations. In some cases, plantation managers aimed to burn the fynbos adjacent to the plantations as soon as
it could burn.
It is clear that fire management in the GRCMs has, since the establishment of the plantations until the early 1990s, been primarily aimed at the protection
of commercial timber resources (Table 2). Although it is unlikely that catchment managers managed to execute prescribed burning every time and everywhere as
planned, it seems reasonable to assume that large parts of the GRCMs’ fynbos have at times been burnt at shorter fire return intervals, and lower
intensities, than those deemed ecologically desirable for fynbos conservation. Both frequent and low intensity fires in fynbos and other Mediterranean-climate
shrublands favour resprouters over slow-maturing reseeders.59,60 This preference may account for the dominance of graminoid sprouters and the paucity
of slow-maturing reseeding shrubs of the Proteaceae family in parts of the GRCMs, particularly in areas near plantations (Kraaij T, personal observation).
With regard to fire season, prescribed burning has mostly been carried out during spring, summer and early autumn (October to April) in order to avoid the
winter berg wind season (May to September) associated with conditions of high fire danger and an increased risk of uncontrollable fires (Table 2).
The conflict of interest in terms of fire management (fire return periods in particular) in the GRCMs has been brought into sharp focus by the separation of
plantation and catchment management functions within DoF, and later the privatisation of plantations and handover of catchment management to conservation
agencies. Catchment management has further been complicated, ecologically and economically, by the extensive infestations of invasive alien plant species
(particularly Pinus spp.) almost exclusively sourced from adjacent plantations, with hardly any invasive alien plant control carried out in the
‘no-man’s land’ in almost two decades61 (Figure 2).
Sound ecological management of fires in the study area is constrained by various factors. Repeated institutional disruptions, that is, transfers of DoF
between different state departments and changing land management agencies, resulted in poor record preservation and data continuity. The history of fires
in the study area has therefore been inadequately documented. Fynbos fire ecology in the south-eastern CFK is poorly understood in terms of appropriate
fire season and return interval.15,22 Moreover, fundamental conflict exists between fire intervals required for the reduction of fire hazard to
commercial timber plantations, and those deemed necessary for the conservation of fynbos diversity.6,23
Negative feedback mechanisms between fire, alien invasive trees and water resources threaten the achievement of the goals of sustained yields of
water48 from the GRCMs, which are important catchment areas.53 Fire behaviour and ease of access for the
purposes of prescribed burns or fire fighting are negatively affected by the invasion of fynbos by alien shrubs and trees. The invaders increase
fuel loads and consequently fire intensity, particularly under extreme conditions.62 Extreme fire intensities increase the risk to
infrastructure and assets (such as plantations) and fire fighters, and detrimentally affect post-fire recovery of fynbos, soil and water
conservation.63,64,65 Alien pines are spread and proliferated by fire,42 which in turn exacerbates their detrimental impacts.
Areas in close proximity to plantations, where fire safety measures in the GRCMs ought to be focused, are often the worst invaded, thereby rendering
prescribed burning and fire fighting operations impossible. Pines had invaded 54% of the catchment of the Keurbooms River in 1999 to some degree, causing
an estimated 22% reduction in river flow.66 It was further estimated that in the absence of management intervention, the invasions could
potentially occupy 77% of the catchment by 2025, with a projected flow reduction of 95%.66
Past neglect of fire and alien plant management in large parts of the GRCMs has left current conservation agencies financially incapable of correcting
the situation given normal operational funding, and thus unable to fulfil their primary mandate of conserving biodiversity. Previous joint government
ownership and management of plantations and surrounding catchment fynbos fostered the expectation that contemporary fynbos managers should provide protection
from fire to adjacent commercial plantations – at a considerable cost to the former. This political and institutional legacy yielded a plantation
industry which is commercially and environmentally unsustainable44,56 in the absence of subsidisation in the form of fire safety management and
alien plant control on adjacent land. Even with government subsidisation (prior to the 1990s), and without taking on the costly burden of catchment management
(during the period of neglect of the ‘no-man’s land’), SAFCOL plantations in the Western Cape Province operated at a financial
loss.44 This financial situation is why a buyer could initially not be found at the time of privatisation56 and why the decision
was taken to phase out plantation forestry in the area.40,41,44,54
Sustainable management at landscape scale
Sustainable management of the current conservation-plantation matrix will not be achievable in the study area if the continual invasion of the
surrounding landscape by self-sown timber species is not controlled.53 The current environmental and social certification system (the
Forestry Stewardship Council, FSC), adhered to by the plantation industry67 inadequately appraises environmental accountability (i.e.
spread of invasive trees and their impact on water resources) beyond the borders of the plantation management unit. Indeed, in 2004, environmental
NGOs requested that a moratorium be placed on further certification of plantations worldwide, which led to a review of standards for FSC certification
of plantations.41,68 The development of new standards and the implementation of trial audits have not resolved this issue, which remains
contentious amongst FSC stakeholder groups. Whether plantation forestry can be undertaken sustainably in South Africa and whether it should be certified
remains an open question.67 Biological control, which may be seen as the only viable option for the control of vast infestations of invasive
pines in remote catchments, continues to be opposed by the plantation industry.42,69,70 Legislation pertaining to the control of alien invasive
plants is not enforced, whilst a discrepancy between the capacities to enforce legislation pertaining to fire risk management versus invasive plant
control70 intensifies the conflict between the conservation and plantation sectors. This conflict is evident from substantial legal claims
instituted against conservation authorities for fire damage to plantations in recent years (Table 2). Finally, the sustainability of both sectors is
additionally compromised by government’s decision to partially reverse the plantation decommissioning programme.58 The outcome will be
a more fragmented landscape where neither plantations nor protected areas can be suitably consolidated or coherently managed in terms of fire, invasive
plants or general operations44 (Stehle T 2010, personal communication, November 25).
The challenges associated with managing the new national park are substantial, and knowledge and solutions are not always available, which indicates
the need for further research. Firstly, understanding of the historical fire regime in the area and how it has changed during the past century71
has to be improved through the creation and analysis of a database of historical fire records.72 Ongoing accurate mapping of future fires is
furthermore necessary to serve as a basis for the design of natural experiments and fire management decisions.28 Secondly, the ecological
requirements of eastern coastal CFK fynbos in terms of fire season and minimum fire return intervals need to be determined. To this end, post-fire recruitment
success and youth periods of slow-maturing reseeding species (e.g. the Proteaceae16,18) should be studied. Similarly, the youth periods of invasive
pine species need to be established under local conditions. In combination, these should inform fire management guidelines aimed at facilitating fynbos
conservation and invasive pine control. It should furthermore inform thresholds73 within which fire managers can attempt to resolve the conflicting
demands of fire hazard reduction and biodiversity conservation. Thirdly, a legal review should be conducted to consider the practicalities of implementing fire
legislation in the face of conflicting land management objectives (fire risk vs. biodiversity conservation). The respective responsibilities applicable
to the conservation and commercial forestry sectors in terms of fire and invader plant legislation need to be clarified. This clarification should facilitate
cross-cutting compliance and cooperation without the need for costly legal action. Lastly, resource economics research should further explore alternative
funding for alien plant clearing initiatives in watersheds. Approaches based on payment for ecosystem services38 should be expanded, targeting
major water users, such as agricultural industries, municipalities and the tourism industry. Cost–benefit analyses need to compare the environmental
and socio-economic advantages of invasive plant clearing versus desalinisation of sea water as different means to secure water supply to water-stressed
coastal towns39 (Preston G 2010, personal communication, October 01).
Management interventions to be considered
Land owners and managers in the area need to realise that fynbos and plantations cannot be fire-proofed.71 It has been shown for fire-prone
shrublands and forests across the globe that large fires are not dependent on a build-up of fuel, and therefore frequent burning to reduce fuel loads
will not necessarily reduce the risk of runaway wildfires.27,74,75,76 The combination of fire danger restrictions and financial constraints
furthermore makes large-scale prescribed burning of catchment vegetation unattainable.27 The most effective strategy for facilitating fire
safety where necessary is to focus effort on (limited) strategic locations. A legal review should furthermore clarify the respective responsibilities
of the conservation and forestry sectors under current fire legislation. Official agreements between neighbouring land managing agencies should clearly
stipulate fire management protocols, and should be formalised within regional Fire Protection Agencies.
Invasive plant control
The timber industry should recognise its legal responsibility to control the spread of invasive alien trees from their plantations in terms of the
Conservation of Agricultural Resources Act.42 The South African government proposed the introduction of a seed pollution levy on the
forestry sector in 2005 under the National Environmental Management Act: Biodiversity Act, which has been vehemently opposed by the industry on
account of its potential economic impact and because it is perceived as discriminatory.77 Plantation forestry in the Cape has in the past
externalised its environmental costs, and continues to do so by not taking sufficient responsibility for invasive plant clearing beyond plantation
borders and by leaving the task to the neighbouring conservation agencies.44 As the intention of government is now clearly to separate the
functions of commercial forestry and conservation, the former has an obligation to the latter to offset these previously externalised costs, as government
has been cautioned to ‘not end up subsidising a single business’44. Nonetheless, a ‘polluter pays’ policy remains to be
implemented, possibly through the imposition of a levy on timber products.42 Likewise, the FSC and other certification bodies should consider
adopting stricter criteria for the mitigation of the negative effects of invasive trees beyond the borders of forestry estates.42,67 The best
approach to management of invasive alien plants would be to integrate various control methods.35 Options include (1) manual clearing; (2)
manipulation of disturbance regimes, i.e. fire; (3) future planting of less invasive species and/or sterile varieties; and (4) allowing the release of
host-specific, seed-attacking biological control organisms for invasive Pinus species.42 Biological control for pines has been
considered,78 but, in a highly conservative move, has been abandoned for fears that it could potentially be detrimental to the forest
The invasive pine problem in the GRCMs is an example of ‘invasion debt’79 where the current pattern of invasion primarily reflects
the historical socio-economic and political legacy. Neglect of the ‘no-man’s land’ during the past 20 years has further aggravated the
invasive plant problem. Government appropriately stated in its White Paper on sustainable forest development in South Africa52 that ‘the
costs and benefits of this [the plantation] industry in terms of water resources and the environment in general need to be properly evaluated’ and
furthermore that ‘Government believes that a responsible attitude in forestry would have plantation forests removed from areas where demonstrable
environmental damage has been done’. These statements imply three distinct undertakings by the state: (1) application of sound economic and environmental
standards to the commercial forestry industry (DoF is ultimately responsible for overseeing and regulating the industry25,52); (2) appropriate
allocation of resources for the rehabilitation of decommissioned plantations and neighbouring areas damaged by invader plants historically sourced from
plantations38; and (3) a review of the decision to reverse the plantation decommissioning strategy.44,58 A balanced analysis of the
full public costs and benefits of the plantations, and their economic and ecological impacts and future risks, have to be considered at landscape
scale.54,80 Land use fragmentation needs rationalisation in the interests of both the plantation and conservation sectors. This was the
original intention of DoF with their plantation decommissioning strategy. In this strategy, DoF emphasised the link between plantation withdrawal and
the transfer of other conservation land to SANParks, and required that these processes be well coordinated.57
Owing to successive institutional disruptions in the study area, the collation of fire management related policies, practices and data has been challenging.
Our account constitutes a first qualitative regional history of fire management in the CFK published in the primary literature. Such published accounts will
become invaluable where there is a reliance on tacit knowledge, and particularly where institutional memory is rapidly fading. Fire management in the fynbos
catchments of the new GRNP presents considerable challenges that cannot be overcome without addressing the invasive alien plant problem in the area. In the
short and medium term, substantial resources will be required to correct the situation left by decades of management neglect. Longer-term sustainability of
the region necessitates rationalisation of the currently highly fragmented land use with their conflicting requirements.
We thank all interview respondents for their willingness to share information, knowledge and experience. We appreciate access to the archives of MTO
Forestry and DoF (now Department of Agriculture, Forestry and Fisheries), in particular the assistance of Theo Stehle at the Knysna regional office.
Kobus Venter made documentation available on the plantation decommissioning process. Johan Baard prepared Figure 1 and shared the data contained in Table 1.
The comments of Dr W. Vermeulen and two anonymous reviewers resulted in improvements to the manuscript. We acknowledge SANParks, the Nelson Mandela Metropolitan
University and the Council for Scientific and Industrial Research for supporting this research.
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