Zonation of land or water areas is a tool frequently used to clarify management objectives, assist with monitoring of the effectiveness of those objectives and reconcile user conflicts. The Ramsar Convention has promoted zonation for wetlands as a management tool, but in a rather unstructured way, in contrast to the highly structured three-zone system of UNESCO-MAB Biosphere Reserves. At the same time, over the last 40 years IUCN has been developing a categorisation system for protected areas, currently based on management and monitoring objectives. Research undertaken primarily on wetlands in China, but with desk-top study in other regions has shown that by using these management and monitoring objectives as guiding principles, and building on the Biosphere Reserve zonation system, a new approach is possible for wetland protected or conserved areas. Developing from the three-zone system of Biosphere Reserves this new approach proposes four zones, offering more utility and flexibility for managing, monitoring and comparing wetland conservation sites, both spatially and temporally.
The ideas developed in this paper originate from a series of studies on zonation systems used for management in wetland protected areas of China. Many, but not all, wetland protected areas in China are listed as Wetlands of International Importance under the Convention on Wetlands [
We subsequently undertake a global review, comparing zonation systems proposed and used for wetlands. Building on that review, this paper attempts to explore the issues of zonation in all conserved and managed wetlands, including Ramsar sites. We also link these zonation ideas with the management objectives described under the Protected Area Category Guidelines by IUCN [
Detailed studies on a particular Chinese wetland, Wulangsuhai [
Early studies of zonation, largely in an ecological context, began in the early 1900s with a focus largely on links between climate and vegetation. In wetlands, especially, zonation is often taken also to refer to the spatial or temporal arrangement of vegetation types.
Wetlands are among the most dynamic and productive ecosystems on Earth [
Besides using zonation to describe floristic and structural variation of wetlands in space, and occasionally time, in recent decades zonation has been used as a management tool across terrestrial and aquatic ecosystems, key examples being in fisheries, and marine and terrestrial protected areas [
In wetlands specifically, conservation and natural resource managers have used zoning as a useful device in allocating management effort and attention, and as means of creating coarse divisions for monitoring and managing wetlands as a landscape feature, especially those designated internationally under the Ramsar Convention or under national law. Since its creation in 1975 the Great Barrier Reef Marine Park (Australia) has moved towards a more detailed yet responsive zonation system, with greater precision on no-take zones, which helps fishers plan their activities. Its scheme encompasses seven zones that Chape et al. [
Terminology relating to what a wetland is and the many forms of wetlands has become compounded and more confused in recent years, following the adoption of the terminology used by Convention on Biological Diversity (CBD), i.e. “Inland Waters” (which comprehends saline and alkaline inland lakes). At the same time some NGO’s (e.g. WWF) use “freshwater” or “freshwaters” (which excludes saline and alkaline lakes) as descriptors for this ecosystem category. The Ramsar Convention defines wetlands as “areas of marsh, fen, peatland or water, whether natural or artificial, permanent or temporary, with water that is static or flowing, fresh, brackish or salt, including areas of marine water the depth of which at low tide does not exceed six metres” [
Zones for key management activities in terrestrial conservation reserves are most frequently described as “core” or “buffer”, where “core” implies a strict management regime, often protection through legal or other effective means, and “buffer” is used for an area with “low impact” human activity that enables the strict management of the core to be fully effective. More complex zonation regimes have been developed, especially in the marine realm [
As the key global convention dealing with conservation and management of wetlands, the Ramsar Convention might be expected to have well-defined views on wetlands. And so the first formal discussion of zonation under the convention appears in a recommendation of the Fifth Conference of the Parties (COP) to the Ramsar Convention (Kushiro, Japan): Recommendation V. 3—The Essential Character of Wetlands and the Need for Zonation Related to Wetland Reserves [
Recommendation V. 3 brought the key Ramsar concept of ecological character into the discussion—and this issue was discussed further in considerable detail at Ramsar Conference of the Parties (COP) IX in Kampala, Uganda [
Resolution IX.1 Annex A, elaborated ecological character as:
“....the combination of the ecosystem components, processes and benefits/services that characterise the wetland at a given point in time.”
The same Resolution linked another key Ramsar concept (wise use) and ecological character in the following definition:
“Wise use of wetlands is the maintenance of their ecological character, achieved through the implementation of ecosystem approaches, within the context of sustainable development.”
So, from COP V to IX we have zonation being linked to management, and thus ensuring maintenance of ecological character and, in effect, the ensuring wise use (equivalent to the more modern term sustainable development) of the wetland [
In China, Ramsar listed wetlands, as well as other wetland protected areas, typically have a 3-part zonation, similar, but not identical, to the UNESCO Biosphere Reserve system [
As defined in the Statutory Framework for the World Network of Biosphere Reserves [
Conservation—contributing to of landscape, ecosystem, specie and genetic conservation;
Development—enhancing human well-being and development which is socio-culturally and ecologically sustainable;
Logistic—providing support for research, monitoring, education and information exchange.
Originally these functions were allocated to the three zones, with very little overlap. But as we understand more about ecosystem processes and the delivery of ecosystem goods and services at landscape level (see inter alia [
Buffer zones have a special role—to minimize negative and external effects of human—induced activities on the core areas. In addition to buffering the core area for extensive human activities, buffer zone scan have their own intrinsic functions for maintaining anthropogenic, biological and cultural diversity. Buffer zones also have an important function in promoting connectivity for biodiversity between the core, transition and the wider land/seascape.
This zonation concept is applicable to all Ramsar sites which are also Biosphere Reserves [
Management activities | Core | Buffer | Transition |
---|---|---|---|
Conservation | |||
Legal status for zone | √ | ||
Conserve biodiversity | √ | M | |
Monitoring | √ | M | M |
Non-invasive research | √ | √ | √ |
Logistic | |||
Non-invasive education | √ | √ | √ |
Environmental education | √ | ||
Basic/applied research | √ | M | |
Development | |||
Tourism | √ | ||
Recreation | M | √ | |
Agriculture | √ | ||
Sustainable forestry | M | √ | |
Small settlements | √ | ||
Sustainable development actions (ecosystem service provision) | M | M | √ |
Note: √: the original distribution of functions among the zones; M: function and zone interaction recognized after the Biosphere Reserve meeting in Madrid, Spain, 2006.
IUCN defines [
“A clearly defined geographical space, recognised, and dedicated and managed, through legal or other effective means, to achieve the long-term conservation of nature with associated ecosystem services and cultural values”.
This is different from the simpler definition under Article 2 of the CBD—“a geographically defined area which is designated or regulated and managed to achieve specific conservation objectives” [
IUCN [
The six IUCN categories are used in different ways to achieve conservation goals suitable to the location.
Further complexity is evident when wetlands are considered in a broader landscape context [
“Inland water systems are part of the larger terrestrial landscape and distinct parts are linked to their upstream catchments through a variety of above- and below-ground hydrological processes. The prospect of “fencing off” wetland systems is in most cases technically infeasible. The most effective protected areas for inland water conservation will be part of integrated river basin management (IRBM), sometimes called integrated catchment or watershed management. IRBM involves a landscape-scale strategy to achieve environmental, economic and social objectives concurrently. IRBM is a form of the Ecosystem Approach, which the State Parties to the CBD have committed to implement.”
Management objective | IUCN protected area category | ||||||
---|---|---|---|---|---|---|---|
Ia | Ib | II | III | IV | V | VI | |
Scientific research | 1 | 3 | 2 | 2 | 2 | 2 | 3 |
Wilderness protection | 2 | 1 | 2 | 3 | 3 | - | 2 |
Species/genetic diversity preservation | 1 | 2 | 1 | 1 | 1 | 2 | 1 |
Maintenance of environmental services | 2 | 1 | 1 | - | 1 | 2 | 1 |
Protection of natural/cultural features | - | - | 2 | 1 | 3 | 1 | 3 |
Tourism & Recreation | - | 2 | 1 | 1 | 3 | 1 | 3 |
Education | - | - | 2 | 2 | 2 | 2 | 3 |
Ecologically sustainable use | - | 3 | 3 | - | 2 | 2 | 1 |
Maintenance of cultural attributes | - | - | - | - | - | 1 | 2 |
Note: 1: primary objective; 2: secondary objective; 3: potentially applicable objective; -: not applicable.
Large-scale landscape management, ensuring human benefits from the ecosystems being conserved and managed, and contributing to biodiversity conservation, are all imperatives for today’s ecosystem planner and manager. But we need a more precise way to establish and describe zones used in planning and management, preferably, as noted above, within the Ecosystem Approach of the CBD [
A key conclusion is that Biosphere Reserve nomenclature of Core, Buffer and Transition, while long established does not, in fact, live up to the exacting standards of today’s conservation needs, and needs revision and re-focusing, especially for use in wetlands ecosystems. One key area is the involvement of local people in managing any protected in which they may live. While zonation can cause confusion to local people, it can also offer a way to create awareness for them of conservation needs. CIFOR [
the process of zoning has been implemented rigidly, not adaptively;
there are too many different zones based on unclear criteria, open to wide interpretation;
the legal framework only accommodates one type of community (that present before the park was designated), while in reality there are many communities with different relationships and rights to the park area.
Taking account of all the above, and the fact that many recent Ramsar site nominations have been large areas that include other forms of land use and land categorisation than wetlands, it is clear we need a new paradigm for management zonation in wetlands.
In simple terms, our approach has been to create a three, rather than two, zone system for the buffer zone/ transition area. This will then allow for greater flexibility in developing management objectives taking into account both spatial and temporal ecological variation in the wetland under consideration.
Management objective | Zone 1 | Zone 2 | Zone 3 | Zone 4 |
---|---|---|---|---|
Legal status for zone | Yes | Maybe | No | No |
Scientific research | e | p | n | n |
Species/gene conservation | e | e | p | o |
Cultural features conservation | o | o | o | o |
Geodiversity conservation | o | o | o | o |
Eco-tourism | - | o | o | n |
Broad-scale tourism | - | - | o | n |
Recreation | - | - | - | o |
Sustainable harvesting | - | o | o | n |
Education activities | o | p | p | n |
Agriculture | - | o | o | n |
Sustainable forestry | - | - | - | o |
Settlements (in scale of landscape) | - | - | o | n |
Evolutionary possibilities for biodiversity | e | p | p | o |
Provisioning ecosystem services | n | o | p | p |
Regulating ecosystem services | e | e | p | p |
Supporting ecosystem services | e | e | e | e |
Cultural ecosystem services | n | o | p | p |
Note: e: essential conservation management function; n: non-threatening management function; o: optional management function; p: priority conservation management function; -: inapplicable management function.
In zoning wetlands for management, much depends on two key variables: size and complexity (or, more simply, heterogeneity). It is therefore likely that not every wetland will need all four zones, i.e., a wetland management plan could consist of zones 1, 2 and 4, or 1, 3 and 4, or even just 1 and 4, if the management regime is robust enough [
Ramsar Resolution VIII. 14 had some advice on establishing wetland zonation, including:
Zonation should be established with the full involvement of stakeholders, including local communities and indigenous peoples. Those who neglect essential rural livelihoods and sustainable resource utilization are most likely to foster antagonisms;
A full and detailed rationale should be made to explain the basis for establishing and delineating zones and this is particularly important when establishing the limits of buffer zones;
A concise description of the functions and/or restrictions applied within each zone must be prepared as part of the management plan;
Zones should be identified with a unique and, if possible, meaningful code or name: but in some cases, a simple numerical code may be adequate;
A map showing the boundaries of all zones must be prepared using a Global Positioning System (GPS) where possible to avoid ambiguity, and using obvious geographical features so the boundaries can be easily recognized in the field by managers and wider public alike.
In practical terms, a zonation structure can be established using maps or aerial photographs of the wetland. If the model described above is to be used, then a simple method of allocating major management needs for the wetland can be achieved as follows:
Cover the map or aerial photograph with a grid of suitable size, which will depend on the size and scale of the wetland under consideration;
For each grid cell the management objectives can be summarized, using the matrix of zones and management objectives as shown in
For those cells with mostly Zone 1 objectives, they form Zone 1; mostly Zone 2 objectives zone 2-and so on.
After this analysis a draft zonation map can be produced, field-tested, and then a final map developed with the required precision. It should be noted though that often precision is unhelpful and boundaries that are fuzzy or flexible can be more helpful to a manager, and assist stakeholders discharge their responsibilities. While the zones and objectives are presented as fixed spatial entities, because of the dynamism typical of wetlands discussed earlier, if sustainable utilization is in place, then the zones can be used also to control management in a temporal way.
For example, a wetland zone 3 in which there is a sustainable fishery might be given zone 1 status at some times of the year to ensure adequate reproduction potential for the fish. Zone 3 also has the best potential for providing connectivity within the wetland reserve, while Zone 4 has the best potential for connectivity with the adjacent landscape. Zeng et al. [
Zones described using local vernacular terms, however vague, can assist local stakeholders and immediate ma- nagers understand more effectively what management is required to be undertaken. We note, however, that vernacular names for zones which relate to specific management options do not imply any particular common values across equivalent wetlands. That said, there may well be a local issue where a zone or zones are seen to be important for over-riding management or conservation objectives, feeding or breeding space for migratory waterfowl, and contributing to integrated management at catchment or coastal zone level, and so on.
The abstract naming of zones 1-4 may offer neutrality, and may remove pre-conceptions about the nature of the Zone. However, IUCN attempted such a neutral approach in developing its protected areas categories in 1994, but this proved to be a failure, as there was a clamour for a “common name” to be used besides the Category type! Indeed, many managers would prefer to have a name for the zones they have to allocate and manage.
Embracing both viewpoints, and in order to offer plain language names for the four zones proposed in this paper, we suggest the following reflecting the key management purposes for the zones:
Zone 1—core (high conservation, legally or effectively protected) zone;
Zone 2—limited use zone;
Zone 3—wise use zone;
Zone 4—risk control (connectivity) zone.
Zone 2 and Zone 3 have especial role—to minimize negative and external effects of human-induced activities on Zone 1. They can have their own intrinsic functions for maintaining anthropogenic, biological, cultural diversity. And besides, they can also have an important function in promoting connectivity from Zone 1 to Zone 4 and beyond the wider land/seascape. Such connectivity is now recognized as critical to the development of resilience and coherence in protected area networks [
It seems clear that in managing wetlands, whether protected by Ramsar designation, as part of UNESCO Biosphere Reserves, declared under national law, or existing simply as part of a non-protected but managed landscape feature, zonation can be a useful aid in allocating management effort and attention. But as a management tool to reconcile different user conflicts in protected areas more generally, zonation concept and practice do need better focus; we hope the ideas in this paper go some way towards providing that focus.