About the Author(s)

Jaco Barendse symbol
Scientific Services, South African National Parks, South Africa

Sustainability Research Unit, Nelson Mandela Metropolitan University, South Africa

Dirk Roux Email
Scientific Services, South African National Parks, South Africa

Sustainability Research Unit, Nelson Mandela Metropolitan University, South Africa

Waldo Erfmann
Biodiversity and Social Projects, South African National Parks, South Africa

Johan Baard
Scientific Services, South African National Parks, South Africa

Tineke Kraaij
School of Natural Resource Management, Nelson Mandela Metropolitan University, South Africa

Cara Nieuwoudt
Sharples Environmental Services, Cape Town, South Africa


Barendse, J., Roux, D., Erfmann, W., Baard, J., Kraaij, T. & Nieuwoudt, C., 2016, ‘Viewshed and sense of place as conservation features: A case study and research agenda for South Africa’s national parks’, Koedoe 58(1), a1357. http://dx.doi.org/10.4102/koedoe.v58i1.1357

Original Research

Viewshed and sense of place as conservation features: A case study and research agenda for South Africa’s national parks

Jaco Barendse, Dirk Roux, Waldo Erfmann, Johan Baard, Tineke Kraaij, Cara Nieuwoudt

Received: 04 Sep. 2015; Accepted: 29 Mar. 2016; Published: 05 Aug. 2016

Copyright: © 2016. The Author(s). Licensee: AOSIS.
This is an Open Access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.


Sense of place (SoP) refers to the meanings and values that people attach to places. The concept can be used to frame how people engage or form a connection with the natural environment. At a sensory level, SoP is influenced by people’s visual experiences, which in turn can be linked to the concept of viewsheds. Viewsheds can be transformed, either abruptly (e.g. by infrastructure development such as wind turbines) or more gradually (e.g. by non-native trees invading a landscape). In this study, we focus on the Garden Route National Park to explore the potential importance of viewsheds as a conservation feature, specifically in the context of non-native (especially invasive) tree species. Using mixed information sources, we explore the potential role of invasive trees on experiences of visitors to this protected area and speculate on how viewsheds may shape SoP associations and how such associations may inform protected area management. Our investigation shows that people’s experiences regarding natural and modified viewsheds are varied and intricate. Both SoP and viewsheds have the potential to inform conservation action, and these concepts should form an integral part of objective hierarchies and management plans for national parks. However, while legislation and park management plans make provision for the use of these concepts, associated research in South Africa is virtually non-existent. We conclude by proposing a conceptual model and research agenda to promote the use of viewsheds and SoP in the management of national parks in South Africa.

Conservation implications: Viewshed and sense of place can be used as boundary concepts to (1) facilitate interdisciplinary research between social and natural scientists, (2) help understand the connectedness and feedbacks between people and nature and (3) promote communication between science, management and stakeholders regarding desired conditions of landscapes in and around parks.


A growing number of scientists believe that Earth has transitioned into a new geological epoch – the Anthropocene – characterised by a single, dominant species (Homo sapiens) that is affecting the planet’s life support system at an unprecedented scale, including changes to landscapes and ecosystems, biological distributions, climate and atmospheric chemistry (Steffen, Crutzen & Mcneill 2007; Zalasiewicz et al. 2010). The proclamation and effective management of representative networks of protected areas (PAs) is seen as critical to buffering society against adverse changes to the biosphere attributable to this human-dominated era (Watson et al. 2014). In this context, expected benefits from PAs include conserving biodiversity, safeguarding ecosystems and the services they provide, mitigating climate change and promoting social–ecological resilience, with associated economic and social benefits, at regional scales.

There is increasing recognition of the importance of less tangible or quantifiable benefits that people derive from nature and PAs. Such benefits are, for example, referred to as ‘Nature’s Gifts’ in the Intergovernmental Platform on Biodiversity and Ecosystem Services Conceptual Framework (Díaz et al. 2015). These benefits are often grouped under the collective of ‘cultural ecosystem services’, including experiential, spiritual, educational and recreational interactions with nature that contribute to human well-being (Millennium Ecosystem Assessment 2005). Importantly, an appreciation of such benefits is often dependent on a pro-environmental identity or ability to engage or form a connection with the natural environment (Hinds & Sparks 2008), for example, through ‘meaningful nature experiences’ (Zylstra et al. 2014).

How people connect with nature is invariably a function of their value systems (see Chan, Satterfield & Goldstein 2012; Raymond et al. 2009), which are context-specific and evolve dynamically over time. For example, while one group may value a particular landscape for its tangible materials (such as harvestable fruits and medicinal plants), another may value the same landscape for intangible benefits (such as relaxation and therapy) derived from its tranquil and scenic features. For the purpose of this study, we will focus on intangible benefits that people derive through experiential interactions with nature. In this context, connection between humans and nature relate strongly to aesthetics (Plieninger et al. 2015) and therefore link closely with concepts such as ‘viewsheds’ and ‘landscapes’. Perceptions of ‘beautiful scenery’ may be a predictor for environmental connection. Likewise, the sensitivity of ‘the public’ to scenery or ‘how the landscape looks’ is an important driver of support for conservation actions. This is borne out by spatial metrics studies (Palmer 2004) and evidence that positive nature experiences (such as hikes) may predispose people to financially support conservation efforts (Zaradic, Pergams & Kareiva 2009).

Ironically, although the creation of PAs has often led to the separation of humans and nature (West, Igoe & Brockington 2006), these remnants of wilder, more natural or intact ecosystems and landscapes potentially offer greater opportunity to experience connection with nature and benefits such as psychological rejuvenation (see Ulrich et al. 1991). Higher ecological integrity should result in higher ‘visual landscape quality’, and together with the notion of ‘sense of place’ (SoP) and the related concept of ‘place attachment’ (the environmental psychologist’s equivalent of the geographer’s SoP) (Farnum, Hall & Kruger 2005) is subsumed in the landscape-quality construct (Daniel 2001).

Although sometimes regarded as vague (Shamai 1991) and elusive (Williams & Stewart 1998), the concept of SoP has been applied widely to describe the relationship between people and physical environment. It is generally used for framing the meanings and values that people attach to places (Larson, De Freitas & Hicks 2013; Williams & Stewart 1998) and may incorporate experiences of dependence, attachment, identity and satisfaction (Jorgensen & Stedman 2001; Stedman 2003). Such meanings and values are typically rich and varied (Williams & Stewart 1998), commonly based on a mix of cultural histories and natural features in a landscape (Larson et al. 2013), and develop as a result of biological, individual and sociocultural processes that take place while interacting with the physical environment (Hausmann et al. 2016). Many feel that SoP resides primarily in human experiences, interpretations and value endowment, rather than being intrinsic to the physical setting itself – ‘space becomes place when we endow it with value’ (Tuan 1977; but see Stedman 2003).

At a sensory level, what people do (e.g. fish from the bank of a river), feel (e.g. grass under their feet or warmth of the sun), hear (e.g. the sound of birds or the wind in the trees) and see (e.g. a seascape or forest) will contribute to their experiences in relation to a place. Such experiences are likely to change over time (e.g. different seasons) and space (e.g. vantage points) and to be mediated by memory of previous such experiences. While the natural sciences have found ways to measure, for example, changes in soundscapes (Pijanowski et al. 2011) and viewsheds (Camp, Sinton & Knight 1997), neither of these concepts has been incorporated into the predominantly social construct of SoP. Apart from the social variable, there may be many different ways in which SoP can be altered or lost, through changes in physical appearance within a landscape, and thus its aesthetics. Let us consider viewsheds in ‘natural’ or ‘wilderness’ areas, defined in the US Wilderness Act (Public Law 88–577, 16 U.S. C. 1131–1136, 88th Congress, Second Session, September 3, 1964) as:

… undeveloped … land retaining its primeval character and influence, without permanent improvements or human habitation, which is protected and managed so as to preserve its natural conditions and which … generally appears to have been affected primarily by the forces of nature, with the imprint of man’s work substantially unnoticeable; and … has outstanding opportunities for solitude or a primitive and unconfined type of recreation. (n.p.)

It stands to reason that such viewsheds (and associated place-value) may be transformed, or even destroyed, by evidence of human presence or activities. Viewshed transformation can intuitively be linked to structural developments, for example, housing on a lake shoreline (Stedman 2003), presence of roads (Selva et al. 2011) or power infrastructure such as overhead pylons and wind turbines (Gee 2010). However, there are other, less explicit, human-mediated changes. One such ‘slow’ transformer of viewsheds may be non-native plants that have become invasive, especially large, woody, tree species (Figure 1) – widely referred to as weeds, invaders or invasive alien plants (IAPs). While we acknowledge the variety of terms and connotations associated with describing IAPs (e.g. Richardson et al. 2000; Schlaepfer, Sax & Olden 2011), we choose to use the more neutral term ‘non-native’ except when explicitly referring to declared invasive alien species or ‘weeds’ as defined by the Conservation of Agricultural Resources Act (CARA, No. 43 of 1983, and amendments). The impacts of IAPs on biodiversity and ecosystems, and resultant ecosystem service loss, such as water quality (e.g. Chamier et al. 2012; Van Wilgen et al. 2008), are widely known and are often the primary determinants for allocation of funding and human resources to manage invasions (Marais, Van Wilgen & Stevens 2004). Less well understood is the impact of IAPs on cultural ecosystem services, such as mediated through SoP experiences (but see Le Maitre et al. 2011), and this aspect is generally not considered when prioritising areas for IAP clearing and restoration.

FIGURE 1: Non-native trees and invasive alien plants are examples of ‘slow transformers’ (compared to other human developments) of landscapes and viewsheds in and around the Garden Route National Park (also see Figure 3), as shown by photographs taken in different years near the iconic ‘Kaaimansgat’ – where the Kaaimans and Swart Rivers enter the Indian Ocean and located within the western Buffer/Viewshed Protection Zone of the GRNP. The view to the north from the Dolphin Point lookout in 1929 (a) and 2015 (b); the view to the south from next to the N2/Kaaimans Pass, pre-1910 (c), 1927 (d) and 2015 (e) – note cellular phone tower ‘disguised’ as pine tree shown by arrow and insert; and the ‘Map of Africa’ Viewpoint, pre-1910 (f) and in 2015 (g).

In this study, we use an interdisciplinary narrative approach, including the use of various pieces of ‘evidence’ and ‘exhibits’, to explore the potential importance of viewsheds as conservation features, specifically in the context of non-native (especially invasive) tree species. We restrict our attention to the Western Cape, the province regarded as the epicentre for development of awareness about IAPs, mainly because of regional public reverence for the native vegetation of the globally recognised Cape Floristic Region (Bennett 2014). Furthermore, we focus on the Garden Route National Park (GRNP) along the southern Cape coast (Garden Route), a region widely known for its scenic beauty and an example of a PA embedded or integrated within a greater social–ecological landscape. Using mixed information sources, including media, unpublished studies, scientific literature and management documents, we explore the potential role of invasive plants (especially trees) on experiences of visitors to this PA and speculate on how viewsheds may shape SoP associations and the interplay between such associations and PA management. To this end, we present a conceptual model relating the concepts of viewshed and SoP to the high-level objectives in a management plan for a national park in South Africa. Lastly, we propose a research agenda to inform the future incorporation of viewsheds and SoP in park management decisions.

The evolving association between people, non-native trees and sense of place

When considering terms such as ‘naturalness’, or whether non-native trees have a place in natural viewsheds, it is important to acknowledge that associated perceptions develop over time. Societal perceptions influence, and are influenced by, the reigning utilitarian values (e.g. forestry or dune stabilisation) and socio-economic circumstances of the period (Baard & Kraaij 2014). Therefore, sentiments about a specific ‘immigrant species’ may change as a society does, or according to whether it is associated with a negative impact or trait, such as being invasive or harmful (Coates 2007).

Perceptions may further depend on how informed individuals are, their level of knowledge of biodiversity, or on more personal values of aesthetics, or notions of scenic beauty (Dhami & Deng 2010; García-Llorente et al. 2008) (also see Box 1 and Figure 2). A case in point is the black wattle (Acacia mearnsii), arguably one of the most problematic IAP species in coastal areas of the Western Cape, originally introduced to support the tanning industry (Carruthers et al. 2011). Especially for a botanist or invasion biologist today, it may be unsettling to travel through the Garden Route where black wattle, together with other Acacia and Pinus species (see photographs in Cowling et al. 2009), dominate the viewsheds of coastal, riparian, mountain and production landscapes (Henderson 1998). That the wattle is now considered unwanted in this region was not always the case, as shown by a letter written to the George and Knysna Herald on 13 September 1893, titled ‘Wattle growing at Knysna’:

Last Sunday the writer took a stroll ‘over the hills’, but by no means so ‘far away’ to the Nursery at Concordia, and would recommend to those of his fellow townsmen who are blessed with the aptitude for enjoying natures beauties to lose no time in hieing tither ere [hastening there before] the many varieties of acacia lose their magnificent bloom. The wattles are just now simply one blaze of bright yellow, and are really a sight worth beholding. (n.p.)

FIGURE 2: Four scenes, three from around the Garden Route National Park: Views from (a) the ‘Seven Passes Road’ near the Woodville ‘Big Tree’ looking towards the Upper Touw River Catchment; and (b) Donaghy’s Hill (42011’47.04”S, 145056’01.97”E) in the Franklin-Gordon Wild Rivers National Park, Tasmania; (c) The area north of Karatara in the Garden Route National Park, looking towards the mountains traversed by the Outeniqua Hiking Trail; (d) the non-invasive Australian red flowering ‘gum’ trees Corymbia ficifolia in full bloom at Bergplaas forestry station is a common and much-loved sight in the Garden Route; along with related alien Eucalypts (Rejmánek & Richardson 2011; Van Staden 2015) many consider these part of the region’s natural-cultural heritage.

BOX 1: Appreciating natural viewsheds and sense of place (see Figure 2).

The writer then goes on to suggest that establishing wattle plantations in the area would not only provide economic benefits on otherwise ‘idle ground’ or ‘sour waste lands’, but that anyone who has seen them in full bloom (as described) would be supportive of his suggestions, presumably on aesthetic grounds. Indeed, wattle growing did become an important economic mainstay in the region well into the 1960s and was strongly supported by the local authorities, as shown by a piece titled ‘The Municipal wattle plantations’ in 03 June 1914 edition of The Herald:

The public of George will learn with pleasure that at the last meeting of the Municipal Council it was unanimously resolved to prepare another 6 morgen of land for the planting of wattle. This is a move in the right direction and if steadily persevered in, this City will find itself within a few years the owner of a very valuable asset … (n.p.)

The above example shows that the lower value attributed to local landscapes and vegetation and the higher value to the non-native species played an important role in promoting their deliberate spread. Contrast this with the present-day situation, where A. mearnsii is now one of the top invaders in the Garden Route (Baard & Kraaij 2014) of especially riparian habitats (Holmes et al. 2005). Country-wide, it has cost an estimated R62 million from 1997 to 2006 to control invasions by Acacia spp. alone (Marais & Wannenburgh 2008) through national initiatives such as Working for Water.

The ‘duality’ in perspective on whether invasive species are ‘good’ or ‘bad’ has a strong cultural dimension (Tassin & Kull 2015) and ties closely to the leading discourse at any given time (Bennett 2014; Carruthers et al. 2011), but it can also vary between different industry sectors, for example, forestry and conservation. In King’s 1951 paper ‘Tree planting in South Africa’, he stated:

There is a small section of the population who wage a wordy warfare against the planting of exotic trees. This element with fanatical zeal, presents only one side of the picture. Let us look at the other side. Criticism is often levelled against wattles on the Cape flats and pines on the mountains of the Cape peninsula. In order to put the matter in proper perspective we must go back to the time when much of the Cape flats was a barren waste of drift sands and the only trees on the mountains were contained in small patches … [on the Cape flats there are] … Only shrubs called blombos (Metalasia) and waxberry (Myrica) both of which are much less valuable than the Australian wattles … [that] yield excellent firewood. Can anyone be so foolish as to imagine that without wattles a population starved for firewood would not have stripped the mountains of woody vegetation? The claim can safely be made that indirectly the wattles have saved the mountain flora from extermination. (p. 13)

In a similar vein, King (1951) stated the following about pines:

Despite their high intrinsic value, pines have been described as weeds, mainly on the grounds that they tend to spread. This is only true of Pinus pinaster, which can readily be kept in check. The allegation that pine plantations are ousting indigenous vegetation is not entirely true, but, even if it were, it cannot be taken seriously, because the plantations occupy less than 3,000 of the 120,000 acres in the [Cape] peninsula. (p. 14)

While these remarks may appear naïve given (expert) knowledge about the current causes, extent and impacts of pine tree invasions (McConnachie et al. 2015), they do represent views that persist to the present, even in scientific circles. For example, a recent ‘Pine plantation vs. Fynbos’ debate (De Ronde 2012) publicly pitched ecologists (Stellenbosch University 2012) against forestry scientists (Du Toit 2012), showing that some perceptions remain entrenched (De Wit, Crookes & Van Wilgen 2001). The article that sparked much of the discussion (Van Wilgen & Richardson 2012) did recognise that exotic conifers may offer aesthetical and recreational benefits to people, especially in peri-urban areas. Such opposing perceptions about non-native species are also pervasive among members of the public, often reflecting incomplete understanding about ecological processes or biodiversity conservation, as shown by 62% of park visitors to the Addo Elephant National Park who did not consider the potential presence of introduced fauna to be in conflict with conservation objectives (Boshoff et al. 2008). Being uninformed can lead to the confusion of unrelated issues, for example, the felling of plantations perceived as synonymous with deforestation of natural forests, or where ‘saving’ a tree – any tree – is seen as positive (Van Wilgen 2012). Perceptions are highly context-specific, for example, species that have been naturalised for a long time are not necessarily perceived as ‘alien’ even by traditional communities (Shackleton et al. 2007); or, despite knowing a species’ alien status, a high utility value may reduce the support for its outright eradication (De Neergaard et al. 2005). This may further vary according to socio-economic variables, where people of higher economic status or better education may rate non-consumptive values of indigenous plants (e.g. aesthetics) higher than poorer or less educated people (Le Maitre et al. 1997). The resultant conflict (between informed and uninformed parties) over non-native species (Dickie et al. 2014) may reduce the potential support for clearing IAPs in PAs, in particular those located close to urban areas, or ‘embedded’ in cities (Van Wilgen 2012).

This does not mean that the potential contribution of PAs in preserving natural viewsheds or landscapes on the basis of aesthetics has escaped recognition. Possibly the earliest local proponent of this cause was Wicht (1943) who – using the cluster pine Pinus pinaster (=maritima) as an example – suggested (almost prophetically, see Cowling et al. 2009; Kraaij, Cowling & Van Wilgen 2011) that exotic plants would, over time, dominate everywhere except in nature reserves and that ‘To botanists and all other lovers of nature the thought that such a change is likely to come is very distressing’ (p. 34). He further suggested that ‘species that are spreading into natural vegetation … [are] undesirable from an aesthetic or scientific view’ (p. 43) and (quoting the Forest and Veld Conservation Act of 1941) that nature reserves should be set aside for the preservation of natural scenery, forests, flora or fauna thereon’ (p. 45) (Wicht 1943).

The above raises three important questions, which we discuss in the ensuing sections, using the GRNP and surrounds as example:

  • Is the preservation of natural viewsheds and associated SoP included or provided for in current national legislation relating to PAs?
  • Do park management plans recognise the potential impact of IAPs on viewshed and SoP as conservation features?
  • Do visitors to PAs value ‘natural’ viewsheds and perceive the presence of IAPs as a threat to SoP in such areas?

Viewshed and sense of place in a protected area context

National legislation

The National Environmental Management: Protected Areas Act (57/2003) (NEM:PA – Norms and standards for the management of PAs in South Africa) stipulates (Chapter 1, p. 3) under guiding principle (a) that PAs should ‘protect ecologically viable areas representative of South Africa’s biological diversity and its natural landscapes and seascapes’; and under (k) ‘contribute to human, social, cultural, spiritual … development’. In Chapter 2 (p. 4), one of the indicators of relative importance is that an area ‘protects a representative sample or iconic feature of South Africa’s land/seascapes’. While provision is made for a zoning plan that determines different activities and conservation objectives within a PA (p. 15), there is no mention of SoP or viewsheds, and the section referring to visitor’s experiences mainly considers visitor facilities (p. 24). In an amendment to NEM:PA (Strategy on Buffer Zones for National Parks, Notice 106 in Government Gazette No. 35020, 08 February 2012) in the context of managing activities in buffer zones surrounding national parks, a viewshed is defined as ‘an area of land, or other environmental element that is visible to the human eye from a fixed vantage point’. In Chapter 3 (p. 12), two of the stated objectives of the policy are to (1) ‘Protect, enhance and restore the unique and memorable character – the SoP – that underpins the image of the national parks and their approaches’; and (2) ‘Protect and enhance the wilderness experience of park users’. To this end, the policy calls for ‘Viewshed protection’ in buffer zone areas that are visible from the park, especially ‘from wilderness areas, or … night lights which negatively effect [sic] the ambience of the park’ (p. 13). Forestry is specifically listed as a development that ‘may have a negative impact or effect on a national park’ (p. 13) and the control of IAPs in buffer zones (p. 19) is mentioned in the context of local community involvement and ecosystem rehabilitation; however, the policy falls short of making the link between the potential impact of IAPs or non-native trees (other than in plantations) on viewsheds, or SoP.

Another area of governance that holds implications for activities in park buffer zones and takes into consideration viewshed and SoP is land-use planning and environmental management. At a national level, the National Environmental Management Act and the Environmental Conservation Act, which guide Environmental Impact Assessments, include visual impact considerations as a component. Further, the National Heritage Resources Act (Act No. 25 of 1999) provides protection for listed or proclaimed heritage resources and sites, such as urban conservation areas, nature reserves, and recognised scenic routes. Western Cape provincial legislation requires the preparation of a Spatial Development Framework (SDF) and an Integrated Development Plan for each sub-region or municipality. These documents aim to guide land-use to be compatible with cultural and scenic landscapes and could include reference to open-space and scenic resources, together with management guidelines for the area covered by these plans, for example, the Knysna SDF (http://www.knysna.gov.za/wp-content/uploads/2012/12/Knysna-SDF-Nov-2008-Core.pdf).

Under these management guidelines, protection is provided not only to existing natural assets such as existing and proposed PAs but also to transformed, so-called ‘Productive Green Areas’, that include existing agricultural and commercial forestry areas, which:

have historically been, and should remain important sources of productive economic activity in the municipal area, as well as being contributors to the sense of place. (n.p.)

This role of SoP and visual amenity of non-native vegetation thus finds legal application (which may be in conflict with the application of NEM:PA) in urban expansion developments. In a recent case at the coastal town of Plettenberg Bay on the Garden Route, a part of a residential development was not granted environmental authorisation in order to retain a stand of mature, non-native Eucalyptus trees alongside an indigenous forest on the same property.

Park management plans

A somewhat more detailed consideration of viewshed is found at the park management plan level. For example, the Garden Route National Park Management Plan (GRNPMP; SANParks 2012) – and in fact all other park management plans – make generic provision for viewshed protection areas and defines a Viewshed Protection Zone as ‘an area where any developments should be screened to prevent excessive impact on the aesthetic appeal of the park’. The GRNPMP recognises five different zones (Table 1, Figure 2) that stipulate limits of acceptable change in terms of aesthetics and recreational activities, including consideration of facilities and infrastructure development and visitor numbers. Although terms such as wild appearance and character’, ‘natural appearance’ and ‘wilderness characteristic’ are used to distinguish between the different types of zones, there is no specific mention of IAPs and their potential influence on the aesthetic appeal in these zones, or visitor’s experiences. We are unaware of any initiatives in the national parks through which viewsheds or the SoP experiences of visitors in relation to viewsheds are being monitored. This might be a function of NEM:PA providing only limited support for monitoring and reporting against progress in implementing plans, with legal obligations to monitor largely confined to the impact of revenue-generating activities.

TABLE 1: Zonation and limitations of acceptable change to aesthetics and recreational activities.
Public perceptions towards invasive alien plants in protected areas

Information on the perception of park visitors regarding the presence of IAPs in viewsheds, or more generally on SoP in South African PAs, appears to be non-existent. Here, we present results from an exploratory and an opportunistic survey. The first was conducted during 2013 in the Knysna Section of the GRNP at three sites: Spitskop Viewpoint and the Fisantehoek and Sinclair Huts on the Outeniqua Hiking Trail (Figure 3). The second opportunistic survey was conducted along the course of the 5-day Tsitsikamma Hiking Trail (in January 2014), which crosses mountain fynbos and indigenous forest areas managed by South African National Parks (Tsitsikamma section of the GRNP) and pine plantations (Cape Pine).

FIGURE 3: The location of the Garden Route National Park Wilderness and Knysna Sections, main geographical features and places, and the Viewshed Protection Zones defined in Table 1, relative density of Alien Invasive Plants within the GRNP and selected points of interest mentioned in the text or illustrated in other figures.

In the first survey, a composite panoramic photograph was taken of the available viewshed at each of the three sites, and each photo was delineated into numbered sections based on the visible extent of IAP coverage (see examples in Figure 4a), but excluding barren areas such as roads. For each of the identified numbered sections, this was equated to actual IAP densities (see Table 1-A1) derived from aerial vegetation cover and transformation surveys (Vlok, Euston-Brown & Wolf 2008) and further classified according to the height class of the predominant vegetation (≤ 2 m or > 2 m) and state of transformation by IAPs, relative to the desired natural state (on a five-point scale, from fully transformed to completely natural). Overnight hikers and day visitors were approached between 08 May and 07 July 2013 and shown a photo of the viewshed (with numbered sections) at the given site. They were then asked to score each section on how it influenced their viewshed experience, where 1 = a reduced experience, 2 = no effect and 3 = an enhanced experience. They were asked to motivate each score: every time IAPs were mentioned, it was recorded against the specific section. The survey was concluded with the question, ‘Why did you specifically choose to visit this site’? If the answer included words or phrases alluding to the aesthetic appeal of the site (e.g. ‘naturalness’, ‘wildness’, ‘prettiness’), it was recorded (see Box 2 and Figure 5).

FIGURE 4: Examples of photographs shown to park visitors to determine viewshed preferences and assess awareness about invasive alien plants: Views at (a) Fisantehoek Hut and (b) Sinclair Hut showing 4 and 10 delineated sections, respectively, to illustrate the methodology used; and composite panoramic photo of the view at (c) Spitskop Viewpoint (11 sections, not shown).

FIGURE 5: Influence on visitor’s experience attributable to (a) vegetation height and (b) state of transformation of the vegetation in perceivable viewshed sections on photographs, combined for three sites. Also indicated is the number of times invasive alien plants were mentioned per vegetation height class or transformation state. The number of respondents who specifically mentioned (c) invasive alien plants per viewshed section or (d) aesthetics per survey site.

BOX 2: Results from visitor surveys in the Knysna Section of the Garden Route National Park.

During the second opportunistic survey, hikers encountered were asked three questions. This was after hiking for at least 2 days through a landscape with a high prevalence of non-native trees, including dense stands of pines (see Figure 6) and wattles in the fynbos sections (see Box 3).

FIGURE 6: Invasive pine trees growing along the Tsitsikamma Hiking Trail may, or may not, impact on the viewshed and sense of place experiences of hikers (Box 3).

BOX 3: Responses of nine hikers on the Tsitsikamma Hiking Trail.

Synthesis of insights

Our varied assemblage of evidence suggests that SoP, although provided for in legislative spheres and by national park and environmental management, remains a poorly developed concept in South Africa. Where and when considered, it rarely relates to a holistic appreciation of viewsheds, landscapes or biodiversity, including non-native trees. Specifically for the GRNP, the extant zonation scheme (Table 1) recognises changes to aesthetics due to human activities, albeit at a very coarse scale, but it does not consider non-native trees or IAPs. The same applies to the demarcated Viewshed Protection Zone (Figure 3) where, ironically, high AIP densities may occur in areas zoned as ‘Remote’ or along the Outeniqua Hiking Trial (Figure 2c), particularly in fynbos vegetation. In buffer zones, our examples show that over the past century, non-native trees have become established features of iconic view sites (Figure 1) and main tourist routes (Figure 2b). This is indicative that wattles and pines continue to form part of a publicly acceptable viewshed, firstly, due to the historic role of these non-native trees in the development of the region, and secondly, due to a lack of a collective mental model of what a representative Garden Route viewshed should look like. Thus, while Le Maitre et al. (2011) argue that invasive Australian acacias can negatively affect both tourist experience and SoP by reducing ‘landscape diversity’ and degrading recreational areas, our exploratory surveys suggest that this relationship is not so straightforward. Even where park visitors were aware of non-natives, such knowledge did not necessarily translate into negative experiences (as suggested by results from our survey – Figure 5a), and it seems that mature (> 2 m) non-native trees may even contribute to positive scenic or aesthetic experiences. Likewise, while some hikers displayed fairly good understanding of invasive pines and alluded to negative experiences, others were apparently oblivious or tended towards absolute biocentricity – simply enjoying any trees (Box 3). Therefore, while scientists may be able to distinguish between ecosystem service benefits offered by initial introductions of non-natives, and ecosystem service losses due to subsequent invasions, this may not be intuitive for non-scientists, especially when such species also provide tangible benefits (e.g. De Neergaard et al. 2005). This may hinder public support or understanding of clearing and restoration efforts.

The same applies at park management level, where managers may be aware of the negative impact of IAPs on biodiversity and provision of ecosystem services, but may not value the preservation of aesthetics (e.g. in California – Funk et al. 2013) or consider the potential impact on tourism (Forsyth et al. 2012) as a reason to combat IAPs. This is similar for attitudes towards non-native ornamental species that are found in rest camps in Kruger National Park (Foxcroft, Richardson & Wilson 2008), where it required education and increased awareness of staff to gain support for the removal of such plants. Similarly, tourists in Pilanesberg who were aware of the invasive prickly pear (Opuntia stricta) indicated a willingness to contribute financially to its control (Nikodinoska et al. 2014). In an ‘open-access’ scenario such as the GRNP where visitors do not necessarily have to pass through a gate to experience the park, the demarcation between PAs, surrounding buffer zones and the rest of the landscape is less easily observable. Given that non-native trees are entrenched as part of the Garden Route’s cultural heritage, it will require a particularly pragmatic (and creative) approach to use feedbacks from visitor SoP experiences to inform park management.

The role of shifting baselines in sense of place

Given how attachment to place and SoP develop over time and is closely related to individual baselines, it is worth considering how the concepts of naturalness or reference states are formed. Retaining historical character of a region may serve as motivation for AIP eradication but over time people become accustomed to non-natives (Schlaepfer et al. 2011). There may be differences between experiences of local and foreign visitors, making ‘novel’ ecosystems more acceptable to some due to a lack of historic perspective, or personal familiarity with similar viewsheds elsewhere.

Internationally, there is some indication that the way in which people appreciate natural areas is evolving. A recent case study in the River Piedra floodplain (Spain), has shown that over the past 50 years, there has been a positive shift towards appreciation of social and cultural ecosystem services, including aesthetics, inspiration and SoP (see Figure 5 in Felipe-Lucia, Comín & Escalera-Reyes 2015). Similarly, land managers of The Nature Conservancy in the USA consider impacts of non-natives on aesthetics at least equally important to degradation of other (provision) ecosystem services (Kuebbing & Simberloff 2015). While restoration and AIP clearing can have positive effects on ecosystem service provision and tourism in certain biomes or vegetation types (e.g. fynbos – Currie, Milton & Steenkamp 2009), the ‘human element’ also needs due consideration. An example from Finnish national parks showed that the natural characteristics such as scenery and biotype diversity are significant determinants of park visitation, along with factors such as recreational opportunities, for example, availability of trails (Neuvonen et al. 2010).

While it is easy to understand the danger of an ‘absolute ecocentric’ attitude (Sharp et al. 2011), which would oppose the clearing of any tree at all costs, a single-minded, negative focus on non-native species without considering other factors may be counter-productive. In the case of the Garden Route, the contribution of non-native trees and plantation forestry to the historic heritage (e.g. ‘flower gums’, Figure 2d) deserves consideration. There are legal mechanisms to guide some of these trade-off situations, such as the ‘Champion Tree’ project by the Department of Agriculture, Forestry and Fisheries (in terms of Section 12 of the National Forests Act of 1998) which recognises individual specimens or clumps of non-native trees of historic value or exceptional size. Also, the South African National Heritage Resources Act (Act No. 25 of 1999) mandates protection of ‘heritage objects’ including natural landscapes of cultural significance; even non-native trees associated with such landscapes, for example, historic arboretums. This emphasises the need for a deliberate process of consultation informed by history, public participation and science to agree on acceptable viewsheds, both native and non-native, that contribute to SoP.

Conceptual framework for incorporating viewsheds and sense of place in the management plans of national parks

In South Africa, the NEM:PA makes it obligatory for authorities responsible for PAs to develop a management plan for each such area, to submit this plan for the approval of the Minister responsible for the environment and to manage the PA in accordance with the approved plan. In the case of SANParks, an adaptive planning approach is followed to formulate a hierarchy of objectives that serve as a basis for developing management plans for the various national parks (see Biggs & Rogers 2003; Foxcroft & McGeoch 2011). Adaptive planning takes place in consultation with relevant organs of state, local communities and other affected parties.

In Figure 7 we propose a conceptual framework for linking the concepts of viewshed and SoP to the typical high-level management objectives of a national park. According to our framework, viewsheds (and other sensory features such as soundscapes) can be described in both biophysical and social or cultural terms. SoP experiences can be viewed as an emergent property of the interaction between people and the environment. Such experiences are mediated by factors such as community history, identity and value systems and can be facilitated or hindered by park management actions. Regarding the latter, there is an obvious interplay between management action and visitor experiences: while conservation initiatives have the potential to build on existing, or to create new, SoP associations (Larson et al. 2013), being aware of SoP experiences can be an effective driver of conservation actions (Ardoin 2014).

FIGURE 7: Schematic showing how viewshed and sense of place relate to a typical set of high-level objectives that serve as a basis for developing park management plans in South African National Parks. Viewshed and sense of place are cross-cutting concepts likely to be influenced via multiple objectives and in turn impact on the Responsible Tourism Objective.

Several arrows in Figure 7 indicate bi-directional influence. Such two-way feedbacks should be important considerations in designing monitoring and management interventions for incorporating viewsheds and SoP into park management plans.

Concluding thoughts and proposing a research agenda

In this article, we have explored the potential impact of IAPs on viewsheds, within a broader context of SoP as experienced by visitors to GRNP. The novelty of our study also results in limitations, in that insights derived from focussing on IAPs, the GRNP and park visitors are not necessarily applicable to other landscape transformers, PAs or sectors of society. However, our study also highlights some pertinent points with generic relevance to PAs in South Africa.

Firstly, the mixed information sources considered in this study suggest that viewshed and SoP are important conservation features from both conceptual and legal perspectives. As such, these concepts need to inform conservation action and therefore should be incorporated into park management plans.

Secondly, viewshed and SoP should be considered through both natural and social lenses to facilitate discussions of the ‘desired future conditions’ of landscapes under conservation from both ecological and social perspectives (Williams & Stewart 1998). To this end, viewshed and SoP can potentially serve as ‘boundary concepts’ to promote interdisciplinary learning between social and natural scientists as well as communication between science, management and stakeholders (Chapin III & Knapp 2015).

Thirdly, the links and feedbacks between conservation features such as viewshed and SoP, disturbances such as non-native and invasive plants and various park management objectives are multiple and intricate. These relationships may straddle human history (shifting baselines) and thus environmental and social contexts. Place-specific monitoring will be required to meaningfully incorporate these concepts into park management practice.

Fourthly, the current lack of formal research in South Africa on viewsheds and SoP, especially relating to national parks and their buffer areas, represents a considerable void in our understanding of the relationship between park management and visitor experiences. Some studies on visitors’ motivations to visit South African PAs have identified activities such as photography (e.g. Saayman, Saayman & Ferreira 2009), implying recognition of scenic values. However, there is a need to explicitly evaluate the role and value of SoP and natural viewsheds in PAs as well as the potential implications that may result from various threats. Threats are likely to be region- and context-specific (e.g. IAPs in GRNP, hydraulic fracturing activities and infrastructure in the Karoo parks and wind farms in coastal areas), further emphasising the breadth of research opportunities.

How do the relationships depicted in Figure 7 play out in the real-world setting of a specific park? We conclude by proposing research questions that could serve as a basis from which to develop a more comprehensive research programme for improved appreciation of viewsheds and SoP as conservation constructs. Firstly, we consider questions related to viewsheds:

  • Considering a broad definition of biodiversity, encompassing genetic, species and ecosystem (including habitat) diversity, could viewshed serve as a surrogate feature (similar to an umbrella species) for conservation?
  • Should South Africa be concerned with conserving a representative sample of natural viewsheds (e.g. per bioregion or biome) and to what degree can or should national parks contribute to such a purpose?
  • What are ‘representative’ or ‘iconic’ viewsheds for specific PAs in terms of historic naturalness and biogeography?
  • How should specific sites for representative and iconic viewsheds be identified? Should such viewsheds be restored where they no longer exist, and which methods should be used to reconstruct acceptable baselines (e.g. soliciting park visitors to submit historic photographs from of chosen sites)?
  • What are the main threats to, and modifiers of, natural or cultural viewsheds and how do these affect SoP experiences of visitors?
  • What is the role of buffer zones in viewshed conservation?
  • Should thresholds of potential concern (TPCs – Biggs et al. 2011) be developed for viewsheds and how could such TPCs inform monitoring (e.g. through fixed-point photography) for compliance with set objectives?

Questions related to SoP are:

  • How should SoP experiences (based on feedback from stakeholders and visitors) be considered in the design, establishment and management of PAs?
  • Can we characterise SoP experiences for each national park and surrounding areas?
  • How do activities, such as guided hikes, animal tracking (e.g. cheetah tracking in Mountain Zebra National Park), trail running and mountain biking (in the GRNP) influence SoP experiences of participating and other visitors to these PAs?
  • How do SoP experiences differ across age groups, cultures and nationalities of visitors, as well as local versus non-local residents, or day versus overnight visitors?
  • Are the dynamics of SoP experiences different in open-access PAs to those in fenced-off PAs with distinct boundaries?
  • What is the relationship between individual and collective experiences in developing attachment to place?

Implementing a research agenda as suggested here could significantly contribute to people-centred conservation while at the same time promoting South African National Parks’ vision of ‘connecting to society’ (http://www.sanparks.co.za/about/connecting_to_society/).


J.B. was supported by a postdoctoral research fellowship from Nelson Mandela Metropolitan University Research Capacity Building and SANParks. We would like to thank Lynne Thompson at the George Research Library for providing historic photographs. We are grateful for helpful colleague reviews from Wessel Vermeulen, Lizette van der Vyver, Marna Herbst, Wendy Annecke, Liandi Slabbert and Peter Bradshaw. We appreciate the constructive comments provided by three anonymous reviewers. The relevant components of this study obtained ethics clearance from Nelson Mandela Metropolitan University (Reference H2013-SCI-NRM-008).

Competing interests

The authors declare that they have no financial or personal relationships which may have inappropriately influenced them in writing this article.

Authors’ contributions

J.B. (South African National Parks and Nelson Mandela Metropolitan University) and D.R. developed the project concept, J.B. (South African National Parks and Nelson Mandela Metropolitan University), D.R. and W.E. were responsible for experimental design, data collection and analyses. T.K. and C.N. made conceptual contributions and literature suggestions. J.B. (South African National Parks) drew the map in Figure 3. J.B. (South African National Parks and Nelson Mandela Metropolitan University) and D.R. wrote the manuscript with contributions by W.E., T.K., J.B. (South African National Parks) and C.N.


Ardoin, N., 2014, ‘Exploring sense of place and environmental behavior at an ecoregional scale in three sites’, Human Ecology 42, 425–441. http://dx.doi.org/10.1007/s10745-014-9652-x

Baard, J.A. & Kraaij, T., 2014, ‘Alien flora of the Garden Route National Park, South Africa’, South African Journal of Botany 94, 51–63. http://dx.doi.org/10.1016/j.sajb.2014.05.010

Bennett, B.M., 2014, ‘Model invasions and the development of national concerns over invasive introduced trees: Insights from South African history’, Biological Invasions 16, 499–512. http://dx.doi.org/10.1007/s10530-013-0601-1

Biggs, H., Ferreira, S., Freitag-Ronaldson, S. & Grant-Biggs, R., 2011, ‘Taking stock after a decade: Does the ‘thresholds of potential concern’ concept need a socio-ecological revamp?’, Koedoe 53(2), 9. http://dx.doi.org/10.4102/koedoe.v53i2.1002

Biggs, H.C. & Rogers, K.H., 2003, ‘An adaptive system to link science, monitoring and management in practice’, in J. Du Toit, K. Rogers & H. Biggs (eds.), The Kruger experience: Ecology and management of savanna heterogeneity, pp. 59–80, Island Press, Washington, DC.

Boshoff, A.F., Landman, M., Kerley, G.I.H. & Bradfield, M., 2008, ‘Visitors’ views on alien animal species in National Parks: A case study from South Africa’, South African Journal of Science 104, 326–328.

Camp, R.J., Sinton, D.T. & Knight, R.L., 1997, ‘Viewsheds: A complementary management approach to buffer zones’, Wildlife Society Bulletin 25, 612–615.

Carruthers, J., Robin, L., Hattingh, J.P., Kull, C.A., Rangan, H. & Van Wilgen, B.W., 2011, ‘A native at home and abroad: The history, politics, ethics and aesthetics of acacias’, Diversity and Distributions 17, 810–821. http://dx.doi.org/10.1111/j.1472-4642.2011.00779.x

Chamier, J., Schachtschneider, K., Le Maitre, D., Ashton, P. & Van Wilgen, B., 2012, ‘Impacts of invasive alien plants on water quality, with particular emphasis on South Africa’, Water SA 38, 345–356. http://dx.doi.org/10.4314/wsa.v38i2.19

Chan, K.M., Satterfield, T. & Goldstein, J., 2012, ‘Rethinking ecosystem services to better address and navigate cultural values’, Ecological Economics 74, 8–18. http://dx.doi.org/10.1016/j.ecolecon.2011.11.011

Chapin, III, F.S. & Knapp, C.N., 2015, ‘Sense of place: A process for identifying and negotiating potentially contested visions of sustainability’, Environmental Science & Policy 53, 38–46. http://dx.doi.org/10.1016/j.envsci.2015.04.012

Coates, P., 2007, American perceptions of immigrant and invasive species: Strangers on the land, University of California Press, Berkeley, CA.

Cowling, R., Van Wilgen, B., Kraaij, T. & Britton, J., 2009, ‘How no-man’s-land is now everyone’s problem. The renowned Cape flora is everywhere in retreat as runaway pine invasions transform the Outeniqua and Tsitsikamma mountains’, Veld & Flora 95(3), 147–149.

Currie, B., Milton, S.J. & Steenkamp, J.C., 2009, ‘Cost-benefit analysis of alien vegetation clearing for water yield and tourism in a mountain catchment in the Western Cape of South Africa’, Ecological Economics 68, 2574–2579. http://dx.doi.org/10.1016/j.ecolecon.2009.04.007

Daniel, T.C., 2001, ‘Whither scenic beauty? Visual landscape quality assessment in the 21st century’, Landscape and Urban Planning 54, 267–281. http://dx.doi.org/10.1016/S0169-2046(01)00141-4

De Neergaard, A., Saarnak, C., Hill, T., Khanyile, M., Berzosa, A.M. & Birch-Thomsen, T., 2005, ‘Australian wattle species in the Drakensberg region of South Africa – An invasive alien or a natural resource?’, Agricultural Systems 85, 216–233. http://dx.doi.org/10.1016/j.agsy.2005.06.009

De Ronde, N., 2012, Pine vs Fynbos, viewed n.d., from http://saforestryonline.co.za/articles/environment/pine_vs_fynbos/

De Wit, M.P., Crookes, D.J. & Van Wilgen, B.W., 2001, ‘Conflicts of interest in environmental management: Estimating the costs and benefits of a tree invasion’, Biological Invasions 3, 167–178. http://dx.doi.org/10.1023/A:1014563702261

Dhami, I. & Deng, J., 2010, ‘Modeling the scenic beauty of the Highland Scenic Highway, West Virginia’, in Clifton E. Watts, Jr. & Cherie LeBlanc Fisher (eds.), Proceedings of the 2009 Northeastern Recreation Research Symposium, pp. 66, Gen. Tech. Rep. NRS, U.S. Department of Agriculture, Forest Service, Northern Research Station.

Díaz, S., Demissew, S., Carabias, J., Joly, C., Lonsdale, M., Ash, N. et al., 2015, ‘The IPBES conceptual framework — connecting nature and people’, Current Opinion in Environmental Sustainability 14, 1–16. http://dx.doi.org/10.1016/j.cosust.2014.11.002

Dickie, I.A., Bennett, B.M., Burrows, L.E., Nuñez, M.A., Peltzer, D.A., Porté, A. et al., 2014, ‘Conflicting values: Ecosystem services and invasive tree management’, Biological Invasions 16, 705–719. http://dx.doi.org/10.1007/s10530-013-0609-6

Du Toit, B., 2012, “No” to biased and pseudo scientific reporting, says Forest Scientist, viewed n.d., from http://blogs.sun.ac.za/news/files/2012/05/Forestry-in-Fynbos-reply-BdT.pdf

Farnum, J., Hall, T. & Kruger, L.E., 2005, Sense of place in natural resource recreation and tourism: An evaluation and assessment of research findings, Department of Agriculture, Forest Service, Pacific Northwest Research Station, Portland, OR.

Felipe-Lucia, M., Comín, F. & Escalera-Reyes, J., 2015, ‘A framework for the social valuation of ecosystem services’, AMBIO 44, 308–318. http://dx.doi.org/10.1007/s13280-014-0555-2

Foxcroft, L. & McGeoch, M., 2011, ‘Implementing invasive species management in an adaptive management framework’, Koedoe 35(2), Art. #1006, 11 pages. http://dx.doi.org/10.4102/koedoe.v53i2.1006

Foxcroft, L., Richardson, D. & Wilson, J.U., 2008, ‘Ornamental plants as invasive aliens: Problems and solutions in Kruger National Park, South Africa’, Environmental Management 41, 32–51. http://dx.doi.org/10.1007/s00267-007-9027-9

Forsyth, G.G., Le Maitre, D.C., O’Farrell, P.J. & Van Wilgen, B.W., 2012, ‘The prioritisation of invasive alien plant control projects using a multi-criteria decision model informed by stakeholder input and spatial data’, Journal of Environmental Management 103, 51–57.

Funk, J.L., Matzek, V., Bernhardt, M. & Johnson, D., 2013, ‘Broadening the case for invasive species management to include impacts on ecosystem services’, BioScience 64, 58–63. http://dx.doi.org/10.1093/biosci/bit004

García-Llorente, M., Martín-López, B., González, J.A., Alcorlo, P. & Montes, C., 2008, ‘Social perceptions of the impacts and benefits of invasive alien species: Implications for management’, Biological Conservation 141, 2969–2983. http://dx.doi.org/10.1016/j.biocon.2008.09.003

Gee, K., 2010, ‘Offshore wind power development as affected by seascape values on the German North Sea coast’, Land Use Policy 27, 185–194. http://dx.doi.org/10.1016/j.landusepol.2009.05.003

Hausmann, A., Slotow, R., Burns, J.K. & Di Mini, E., 2016, ‘The ecosystemn service of sense of place: Benefits for human well-being and biodiversity conservation, Environmental Conservation’ 43(2), 117–127. http://dx.doi.org/10.1017/S0376892915000314

Henderson, L., 1998, ‘Invasive alien woody plants of the southern and southwestern Cape region, South Africa’, Bothalia 28(1), 91–112. http://dx.doi.org/10.4102/abc.v28i1.624

Hinds, J. & Sparks, P., 2008, ‘Engaging with the natural environment: The role of affective connection and identity’, Journal of Environmental Psychology 28, 109–120. http://dx.doi.org/10.1016/j.jenvp.2007.11.001

Holmes, P., Richardson, D., Esler, K., Witkowski, E. & Fourie, S., 2005, ‘A decision-making framework for restoring riparian zones degraded by invasive alien plants in South Africa: Review article’, South African Journal of Science 101, 553–564.

Jorgensen, B.S. & Stedman, R.C., 2001, ‘Sense of place as an attitude: Lakeshore owners attitudes toward their properties’, Journal of Environmental Psychology 21, 233–248. http://dx.doi.org/10.1006/jevp.2001.0226

King, N.L., 1951, ‘Tree-planting in South Africa’, Journal of the South African Forestry Association 21(1), 1–102. http://dx.doi.org/10.1080/03759873.1951.9631082

Kraaij, T., Cowling, R.M. & Van Wilgen, B.W., 2011, ‘Past approaches and future challenges to the management of fire and invasive alien plants in the new Garden Route National Park’, South African Journal of Science 107(9/10), Art. #633, 11 pages. http://dx.doi.org/10.4102/sajs.v107i9/10.633

Kuebbing, S.E. & Simberloff, D., 2015, ‘Missing the bandwagon: Nonnative species impacts still concern managers’, NeoBiota 25, 73–86. http://dx.doi.org/10.1007/s40362-014-0021-3

Larson, S., De Freitas, D.M. & Hicks, C.C., 2013, ‘Sense of place as a determinant of people’s attitudes towards the environment: Implications for natural resources management and planning in the Great Barrier Reef, Australia’, Journal of Environmental Management 117, 226–234. http://dx.doi.org/10.1016/j.jenvman.2012.11.035

Le Maitre, D., Gelderblom, C., Maphasa, L., Sarel, Y., Van Den Belt, M. & Manuel, T., 1997, ‘Communicating the value of fynbos: Results of a survey of stakeholders’, Ecological Economics 22, 105–121. http://dx.doi.org/10.1016/S0921-8009(97)00572-7

Le Maitre, D.C., Gaertner, M., Marchante, E., Ens, E.-J., Holmes, P.M., Pauchard, A. et al., 2011, ‘Impacts of invasive Australian acacias: Implications for management and restoration’, Diversity and Distributions 17, 1015–1029. http://dx.doi.org/10.1111/j.1472-4642.2011.00816.x

Marais, C., Van Wilgen, B.W. & Stevens, D., 2004, ‘The clearing of invasive alien plants in South Africa: A preliminary assessment of costs and progress’, South African Journal of Science 100, 97–103.

Marais, C. & Wannenburgh, A.M., 2008, ‘Restoration of water resources (natural capital) through the clearing of invasive alien plants from riparian areas in South Africa — Costs and water benefits’, South African Journal of Botany 74, 526–537. http://dx.doi.org/10.1016/j.sajb.2008.01.175

McConnachie, M.M., Van Wilgen, B.W., Richardson, D.M., Ferraro, P.J. & Forsyth, A.T., 2015, ‘Estimating the effect of plantations on pine invasions in protected areas: A case study from South Africa’, Journal of Applied Ecology 52, 110–118. http://dx.doi.org/10.1111/1365-2664.12366

Millennium Ecosystem Assessment (MEA), 2005, Ecosystems and human well-being: Synthesis, Island Press, Washington, DC.

Neuvonen, M., Pouta, E., Puustinen, J. & Sievänen, T., 2010, ‘Visits to national parks: Effects of park characteristics and spatial demand’, Journal for Nature Conservation 18, 224–229. http://dx.doi.org/10.1016/j.jnc.2009.10.003

Nikodinoska, N., Foxcroft, L.C., Rouget, M., Paletto, A. & Notaro, S., 2014, ‘Tourists’ perceptions and willingness to pay for the control of Opuntia stricta invasion in protected areas: A case study from South Africa’, Koedoe 56(1), Art. #1214, 8 pages. http://dx.doi.org/10.4102/koedoe.v56i1.1214

Palmer, J.F., 2004, ‘Using spatial metrics to predict scenic perception in a changing landscape: Dennis, Massachusetts’, Landscape and Urban Planning 69, 201–218. http://dx.doi.org/10.1016/j.landurbplan.2003.08.010

Pijanowski, B.C., Villanueva-Rivera, L.J., Dumyahn, S.L., Farina, A., Krause, B.L., Napoletano, B.M. et al., 2011, ‘Soundscape ecology: The science of sound in the landscape’, BioScience 61, 203–216. http://dx.doi.org/10.1525/bio.2011.61.3.6

Plieninger, T., Bieling, C., Fagerholm, N., Byg, A., Hartel, T., Hurley, P. et al., 2015, ‘The role of cultural ecosystem services in landscape management and planning’, Current Opinion in Environmental Sustainability 14, 28–33. http://dx.doi.org/10.1016/j.cosust.2015.02.006

Raymond, C.M., Bryan, B.A., MacDonald, D.H., Cast, A., Strathearn, S., Grandgirard, A. et al., 2009, ‘Mapping community values for natural capital and ecosystem services’, Ecological Economics 68(5), 1301–1315. http://dx.doi.org/10.1016/j.ecolecon.2008.12.006

Rejmánek, M. & Richardson, D.M., 2011, ‘Eucalypts’, in D. Simberloff & M. Rejmánek (eds.), Encyclopedia of biological invasions, pp. 203– 209, University of California, Berkeley, CA.

Richardson, D.M., Pyšek, P., Rejmánek, M., Barbour, M.G., Panetta, F.D. & West, C.J., 2000, ‘Naturalization and invasion of alien plants: Concepts and definitions’, Diversity and Distributions 6, 93–107. http://dx.doi.org/10.1046/j.1472-4642.2000.00083.x

Saayman, M., Saayman, A. & Ferreira, M., 2009, ‘The socio-economic impact of the Karoo National Park’, Koedoe 51(1), Art. #158, 10 pages.

SANParks, 2012, Garden route National Park: Park Management Plan, South African National Parks, Pretoria. viewed n.d., from https://www.sanparks.org/assets/docs/conservation/park_man/grnp-approved-plan.pdf

Schlaepfer, M.A., Sax, D.F. & Olden, J.D., 2011, ‘The potential conservation value of non-native species’, Conservation Biology 25, 428–437. http://dx.doi.org/10.1111/j.1523-1739.2010.01646.x

Selva, N., Kreft, S., Kati, V., Schluck, M., Jonsson, B.-G., Mihok, B. et al., 2011, ‘Roadless and low-traffic areas as conservation targets in Europe’, Environmental Management 48, 865–877. http://dx.doi.org/10.1007/s00267-011-9751-z

Shackleton, C.M., McGarry, D., Fourie, S., Gambiza, J., Shackleton, S.E. & Fabricius, C., 2007, ‘Assessing the effects of invasive alien species on rural livelihoods: Case examples and a framework from South Africa’, Human Ecology 35(1), 113–127.

Shamai, S., 1991, ‘Sense of place: An empirical measurement’, Geoforum 22, 347–358. http://dx.doi.org/10.1016/0016-7185(91)90017-K

Sharp, R.L., Larson, L.R. & Green, G.T., 2011, ‘Factors influencing public preferences for invasive alien species management’, Biological Conservation 144(8), 2097–2104.

Stedman, R.C., 2003, ‘Is it really just a social construction?: The contribution of the physical environment to sense of place’, Society & Natural Resources 16, 671–685. http://dx.doi.org/10.1080/08941920309189

Steffen, W., Crutzen, P.J. & Mcneill, J.R., 2007, ‘The Anthropocene: Are humans now overwhelming the great forces of nature’, AMBIO 36, 614–621. http://dx.doi.org/10.1579/0044-7447(2007)36[614:TAAHNO]2.0.CO;2

Stellenbosch University, 2012, ‘No’ to forestry in fynbos areas, says invasive species specialists, viewed n.d., from http://blogs.sun.ac.za/news/2012/05/17/no-to-forestry-in-fynbos-areas-says-invasive-species-specialists/

Tassin, J. & Kull, C.A., 2015, ‘Facing the broader dimensions of biological invasions’, Land Use Policy 42, 165–169. http://dx.doi.org/10.1016/j.landusepol.2014.07.014

Tuan, Y.-F., 1977, Space and place: The perspective of experience, University of Minnesota Press, Minneapolis.

Ulrich, R.S., Simonds, R.F., Lositio, B.D., Fiorito, E., Miles, M.A. & Zelson, M., 1991, ‘Stress recovery during exposure to natural and urban environments’, Journal of Environmental Psychology 11, 201–230. http://dx.doi.org/10.1016/S0272-4944(05)80184-7

Van Staden, F., 2015, ‘A sticky question: Do gum trees really have to go?’, South Magazine 15, viewed n.d., from http://southmagazine.co.za/archives/2015/a-sticky-question/

Van Wilgen, B.W., 2012, ‘Evidence, perceptions, and trade-offs associated with invasive alien plant control in the Table Mountain National Park, South Africa’, Ecology and Society 17(2), 23. http://dx.doi.org/10.5751/ES-04590-170223

Van Wilgen, B.W., Reyers, B., Le Maitre, D.C., Richardson, D.M. & Schonegevel, L., 2008, ‘A biome-scale assessment of the impact of invasive alien plants on ecosystem services in South Africa’, Journal of Environmental Management 89, 336–349. http://dx.doi.org/10.1016/j.jenvman.2007.06.015

Van Wilgen, B.W. & Richardson, D.M., 2012, ‘Three centuries of managing introduced conifers in South Africa: Benefits, impacts, changing perceptions and conflict resolution’, Journal of Environmental Management 106, 56–68. http://dx.doi.org/10.1016/j.jenvman.2012.03.052

Vlok, J.H.J., Euston-Brown, D.I.W. & Wolf, T., 2008, A vegetation map for the Garden Route Initiative, Unpublished 1:50 000 maps and report supported by CAPE FSP task team.

Watson, J.E.M., Dudley, N., Segan, D.B. & Hockings, M., 2014, ‘The performance and potential of protected areas’, Nature 515, 67–73. http://dx.doi.org/10.1038/nature13947

West, P., Igoe, J. & Brockington, D., 2006, ‘Parks and people: The social impacts of protected areas’, Annual Review of Anthropology 35, 251–277. http://dx.doi.org/10.1146/annurev.anthro.35.081705.123308

Wicht, C.L., 1943, ‘Preservation of the vegetation of the South Western Cape’, Transactions of the Royal Society of South Africa 30, 7–18. http://dx.doi.org/10.1080/00359194309519824

Williams, D.R. & Stewart, S.I., 1998, ‘Sense of place: An elusive concept that is finding a home in ecosystem management’, Journal of Forestry 96, 18–23.

Zalasiewicz, J., Williams, M., Steffen, W. & Crutzen, P., 2010, ‘The new world of the anthropocene’, Environmental Science & Technology 44, 2228–2231. http://dx.doi.org/10.1021/es903118j

Zaradic, P.A., Pergams, O.R.W. & Kareiva, P., 2009, ‘The impact of nature experience on willingness to support conservation’, Plos One 4, e7367. http://dx.doi.org/10.1371/journal.pone.0007367

Zylstra, M., Knight, A., Esler, K. & Le Grange, L.L., 2014, ‘Connectedness as a core conservation concern: An interdisciplinary review of theory and a call for practice’, Springer Science Reviews 2, 119–143. http://dx.doi.org/10.1007/s40362-014-0021-3

Appendix 1

TABLE 1-A1: The density classes (percentage ground cover) and description used in the analysis of results of viewshed zone preference by visitors as surveyed at Spitskop Viewpoint, Sinclair and Fisantehoek Huts.


Crossref Citations

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