The QNP is located in the Baiji Mountains in the northeast of Kaihua County, Quzhou City, Zhejiang Province. It is adjacent to the Wuyuan County of Jiangxi Province and the Xiuning County of Anhui Province. The QNP contains two national natural protection areas, namely Gutian Mountain National Nature Reserve (81.07 km²) and Qianjiangyuan National Forest Park (45 km²), as well as an ecological corridor connecting them (mostly comprising ecological public welfare forests) with a total area of 252 km². The QNP’s objectives are to protect the important representative habitats of the area. These include typical, primitive, large, low-altitude, subtropical evergreen broad-leaved forests, and their living creatures. The ecosystem and landscape are rare in China and the world. The QNP has an obvious hypsographic feature, with an average elevation of about 600-700 m. The highest point is Green Peak (1236 m) in Gutian Mountain. Its water system includes Qianjiangyuan river system and Suzhuang river system. The QNP’s forest coverage rate is 81.70%, mainly concentrating on Qianjiangyuan National Forest Park and Gutian Mountain National Nature Reserve, and the two large areas of forest vegetation are above an altitude of 1000 m, where a lot of wild animals survive, including Elliot’s pheasant (Syrmaticus ellioti) and clouded leopard (Neofelis nebulosa). Apart from these two protected forest areas, other areas are below an altitude of 1000 m. From north to south, there are four villages and towns, namely, Suzhuang, Changhong, Hetian, and Jixi, which include 19 administrative villages, 72 natural villages, and 9744 people. The goal of setting up QNP was to protect the ecological service function of Qianjiangyuan, and the natural ecological system in the central Asian tropical lowland broad-leaved evergreen forests.

The data selected in this paper mainly include：

(1) Data on land use. Based on the vector data of the Second National Land Survey of China, we classified the land use types and ownership to determine the area, utilization types, and spatial proximity of each plot.

(2) Data on settlements and population. We obtained these data as follows: the research team conducted field research in each township and administrative village in QNP, distributing the questionnaires on population data to all village committees, and collecting the numbers of administrative villages and natural villages, as well as the number of settlements and the distribution of major roads. Finally, these data were entered into the main database.

(3) Data on distribution of natural resources. Digital elevation model (DEM) data for the 30-meter resolution of the study area was downloaded from the Geospatial Metadata Website and later integrated into the database for elevation analysis.

(4) Data on the distribution of important species. These data were mainly based on the findings of the terrestrial mammal resources survey of Gutian Mountain and Qianjiangyuan conducted by the Institute of Botany, Chinese Academy of Sciences.

(5) NPP (Net primary productivity). This was obtained by using the natural vegetation NPP model.

Above all, based on the vector data of the Second National Land Survey of Kaihua County, this paper adopted the spatial analysis platform of ArcGIS10.0 to cut down the scope of QNP. Finally, the above data was loaded into the ArcGIS to build the basic database.

Functional zoning mainly involves combining spatial superposition with mathematical statistics (such as cluster analysis, principal component analysis, and factor analysis) (Wall, 1982; Kathirithamby, 2005). Based on the characteristics of natural ecosystem interference in QNP, as well as the sensitivity of the natural ecosystem and ecological pressures on the area (Fu et al., 2017), we designed a comprehensive zoning system by focusing on community and recreation. Meanwhile, considering the importance, systematicness, and availability of the indicators, we finally selected 12 of them for evaluation of the potential habitats, ecological sensitivity, and ecological pressure on important species together with the development opportunities in the study area (Table 1).

Firstly, as ecosystem service is the foundation for the establishment of national parks, we selected the three indicators of carbon sequestration, water conservation, and soil conservation for evaluation.

Secondly, some key nationally protected animals, such as white-necked pheasant, live in QNP, and their existence is an important indicator of the integrity of the regional ecosystem. Therefore, according to the importance of the wild species, 8 species and 3 taxa were screened for analysis. Meanwhile, buffer analysis on habitat was conducted to obtain the potential scope of protection for each species.

Thirdly, since ecological sensitivity reflects the ability of the ecosystem to adapt to human disturbance, and the more sensitive it is, the more vulnerable it is, ecologically sensitive areas are the areas where human activity must be restricted or prohibited. In this study, vegetation coverage, rivers and lakes, topography were chosen to conduct a comprehensive evaluation.

Fourthly, development opportunities reflect the potential of traditional life, recreation, and utilization, and can be expressed in terms of tourism resource density.

Fifthly, ecological sensitivity was calculated according to the natural regional characteristics of QNP, and three levels were created to determine the level of protection, namely, core protection, ecological conservation, and traditional utilization. Simultaneously, considering the community development of residential areas, utilization of ecological resources, and construction of service facilities, we identified the potential for the development of recreation to determine the recreation areas. Finally, the regulatory requirements and specific measures were designed in accordance with the need for protection and utilization.

The ecological characteristics of QNP were analyzed by establishing the evaluation index system of functional zoning. It was found that QNP is rich in vegetation types and includes typical forest vegetation types such as evergreen broad-leaved forests, temperate coniferous and broad-leaved mixed forests, temperate coniferous forests, and evergreen and deciduous broad-leaved mixed forests on mountains and in valleys. What is more, the spatial distribution of the ecosystem service of QNP is obvious, and the value of the ecosystem service is the highest in the Gutian Mountain Nature Reserve and the Qianjiangyuan National Forest Park (which are at each end of QNP), as they preserve the original subtropical low-altitude evergreen broad-leaved forest ecosystem, which is mainly located in the hillsides and foothills 165 to 1246 meters above sea level. In general, the forest coverage rate of QNP is 81.70%, and these forests play an important role in water conservation, soil and water conservation, biodiversity conservation, and air purification. However, in the middle connecting area, the capability of the ecosystem service has decreased significantly. In addition, the ecological corridor connecting the two ends has many secondary forests with a large number of settlements and transport infrastructures, and a certain level of tourism activities has been developed.

As shown in Fig. 2, Gutian Mountain Nature Reserve supports greatest variety of wild animals in QNP, and also possesses important habitats for the priority protected animals of China such as Elliot’s pheasant (Syrmaticus ellioti), hairy-fronted muntjac (Muntiacus crinifrons), clouded leopard (Neofelis nebulosi), and Sri Lankan leopard (Panthera pardus) with large species and population. As for the northern part of QNP, the waters are the habitat for important fish species. With regard to Gutian Mountain Nature Reserve and Qianjiangyuan National Forest Park, the national priority protected plants of Chinese yew (Taxus chinensis), together with the national secondary-level protected plants such as Henry’s emmenopterys (Emmenopterys henryi), Chinese tulip tree (Liriodendron chinense), katsura tree (Cercidiphyllum), and the hardy rubber tree (Eucommia ulmoides) are concentrated in these two regions. However, few wild animals are found in the central area due to the effects of human activities.

According to the ecological sensitivity analysis of QNP, the ecologically sensitive area is moderate in size and mainly concentrated in the Gutianshan and Qianjiangyuan areas (Fig. 3, Table 2). It accounts for 15.7% of the entire study area. The degree of ecological sensitivity of the QNP varies greatly, and it mainly shows medium sensitivity. This category is primarily concentrated in the primeval forest area around the Gutianshan Mountain and Qianjiangyuan Mountain and accounts for 60.92% of the total area. Second, the highly sensitive area, which is mostly secondary forest around the primeval forest area, accounts for 23.53%. The proportions of the mildly sensitive area and the slightly sensitive areas were 14.61% and 0.95% respectively and were mainly distributed in the middle zone. As for development opportunities, these are strictly limited for the Gutian Mountain and Qianjiangyuan areas, and the recreational potential here is small. However, in areas adjacent to the administrative villages of Taoyuan and Hetian, more tourism activities have developed, and there is space for recreational activities and traditional utilization.

In general, the functional zoning of national parks should be based on the characteristics of the natural regional ecosystems, the distribution of community settlements, and the scenic spots. Moreover, the zoning needs to reflect the dominant functions and regional relations, coordinating and controlling the land use to promote the conservation and utilization of resources. As for QNP, it should not only protect the ecosystem of low-elevation evergreen broad-leaved forests in the subtropics, but also meet the needs of large-scale national recreation in the east, and create sustainable livelihoods for a large number of communities in the region, mainly focusing on three aspects: protection, recreation, and community development. According to our analysis of the international approach to the zoning of national parks, it would be appropriate to adopt the four-point method of functional zoning: the core protected area, the ecological conservation area, the traditional utilization area, and the recreational display area. To ensure the integrity of the core protected area, the surroundings should create an ecological buffer zone, separating the core area from community development and recreation utilization. The relationship between functional zoning and ecological sensitivity is illustrated below (Fig. 4). For an ecological geographical unit, the external pressure generated by human activities would have an impact and generate differentiation effects in the ecologically sensitive and non-sensitive regions. Due to the fragility of the systems, the eco-sensitive areas are prone to ecological degradation, while the non-sensitive areas can be adapted to a certain extent and can tolerate human activities. For the ecologically sensitive areas, protection and restoration should be strengthened while, for the non-sensitive areas with attractive landscapes, environmental education and recreation projects with the same development goals as national parks can be carried out appropriately. The areas with attractive landscapes can maintain the status quo and ensure the continuance of traditional production methods and lifestyles.

Figure 5 shows a model of functional zoning for QNP. This is based on the analysis of ecosystem characteristics and ecological sensitivity in different parts of the QNP, taking the protection of representative natural landscapes and habitats of important species as a precondition, and considering future community development and recreation utilization. The functional zone is divided into four parts. Firstly, the strictly protected zone covers 81.32 km² and accounts for 32.3% of the total QNP area. It preserves the original subtropical low-altitude evergreen broad-leaved forest ecosystem and provides suitable habitat for important organisms, a key function of ecosystem service. Secondly, the ecological conservation area, which has an area of 88.54 km² and accounts for 35.17% of the total area, contains an important and fragile primary-secondary forest ecosystem, including relatively large patches of native habitat or areas that have been damaged and require natural recovery. Generally speaking, this area is the ecological barrier and buffer zone for the strictly protected area. Thirdly, the traditional utilization area is 70.49 km², accounting for 28.0% of the total QNP, and it is mainly distributed in the eastern area of Changhong and Qiuxi. There are many economic forests in this area, and the ecosystem’s ecological service capacity is relatively strong. Therefore, this area is suitable for traditional community production and management activities and traditional forest harvesting and breeding. Finally, the recreation area covers 11.39 km² and accounts for 4.53% of the total area. With a large number of tourist resources and good access, this is the area close to where the settlements such as Gutian Village, Qixi, Changhong, and Tianfan are concentrated. In this area, it would be appropriate to facilitate activities such as sightseeing and recreation, science education, and franchising that display the natural and cultural- ecological landscapes of QNP.