To assess the recreational potential, the territories of the research objects were divided into areas with a more or less homogeneous landscape and recreational structure. The territory of forest park plantations in Kamyshin is represented by 30 plots ranging from 1.0 to 15.0 hectares. The “Lapshin Garden” forest park in Volgograd is divided into 7 plots - from 1.5 to 6.0 hectares. The division into sections was carried out mainly by existing communication links (park paths) or by natural or artificial visual boundaries.
The attractiveness of both forest park areas is at a fairly high level: the average value of the attractiveness coefficient of the “Lapshin Garden” forest park (Volgograd) was 0.73, the attractiveness coefficient of forest park plantations in Kamyshin is 0.68 on average. Evaluation of the attractiveness of plantings is usually subjective in nature, since it is associated with emotional,
i.e. sensory perception of the object. The evaluation indicators in the methodology used allow an objective assessment in a quantitative system of points. High ratings are provided, first of all, by indicators of the age and breed composition of the stand. The “Lapshin Garden” (in Volgograd) has an almost homogeneous composition, as the main species are the planting of
Pinus silvestris, the undergrowth and edges are formed by
Acer negundo L.
, Fraxinus americana L.
, Ulmus pumila L., from the bushes of
Cotinus coggygria Scop.
, Frangula alnus Mill. The array was laid in the 50s of the last century, respectively, the age of the plantings is up to 70 years. The considerable age of the stand contributes to the formation of a special emotional image (Fig 3a).
The studied complex of forest plantations located in the city of Kamyshin is not homogeneous (Fig 3b). Its western part (sites 2, 3, 27, 28 and all located to the west) consists of protective plantings of
Pinus ponderosa Douglas ex Loudon,
Pinus laricio subsp. pallasiana (Lamb.) K.Richt
. and their hybrids. Planted more than 100 years ago, the sand-fortifying plantings have turned into a picturesque coniferous forest park. Additional species are
Quercus rubra L. and
Acer platanoides L. The age and condition of the stand provide the plantings with a high indicator of attractiveness.
Plots 1 and 4 represent the collection funds of the arboretum, organized at the arboretum nursery. On the territory of the arboretum there are more than 300 names of taxa with high potential for use in forest reclamation and landscaping plantings, including
Acer L., Quercus L.,
Ðinus, Larix Mill.
, Picea, Juniperus virginiana L.,
Thuja, Celtis occidentalis L.,
Corylus avellana L.,
Tilia L.,
Elaegnus angustifolia L.,
Robinia pseudoacacia L.,
Sorbus L.,
Ulmus L.,
Aesculus hippocastanum L.,
Populus L.,
Padus L.,
Rosa L.,
Fraxinus L.,
Crataegus L.,
Amelanchie,
Viburnum L.,
Caragana arborescens Lam.,
Cotinus coggygria Scop.,
Ptelea trifoliata L.,
Mahonia repens (Lindl.) G. Don
.,
Cytisus L.,
etc. Species diversity contributes to increase in the level of attractiveness, but the high density of the tree stand in most stands, less pronounced layering of homogeneous plantings, as well as clutter with shoots and grass underestimate the assessment the corresponding indicators.
The plots located in the eastern part of the studied massif are geographically adjacent directly to urban development and represent protective forest plantations. The distribution of the value of the attractiveness coefficient by the sites of the studied territories is shown in Fig 4.
The level of comfort of plantings at both sites was determined as average - 0.45. The comfort level indicators chosen by us as evaluative ones determine the set of necessary conditions for the implementation of the recreation function on a landscape object, including the organization of spatial structure, engineering infrastructure and landscaping, the relationship with the external environment. In conditions of arid climate and, accordingly, excessively high summer temperatures and increased insolation conditions, special requirements for the implementation of recreational functions are imposed on the spatial structures of green objects. The ratio of open and closed spatial structures was evaluated for each section of objects according to the canopy closeness parameter. The closeness of the canopy of plantings was calculated as the ratio of the area of the horizontal projection of the canopy of a stand without gaps to the area of the plot
(Moiseev et al., 1990). The projections of the canopy of the stand, as well as the area of the plots, were calculated from satellite images in the Qgis system. The highest 2 points were assigned if the values were 0.7 or more, the 1
st point corresponded to values from 0.3 to 0.69, values less than 0.3 were estimated at 0 points. A significant indicator of comfort is the presence of infrastructure facilities on the territory of the system: A road and path network, equipped places for recreation, observation decks, glades, benches,
etc. At both sites, we have identified only a conditional network of paths formed rather spontaneously by recreants, in accordance with the most popular directions, in easily passable places. Pedestrian communications are most clearly expressed on the territory of coniferous plantings of the forest park in Kamyshin, which confirms the attractiveness of the object for residents of the city. The distribution according to the indicator of the comfort of the studied territories is shown in (Fig 5).
Stability shows an average value, which is explained, rather, not by a high degree of recreational load. Due to the lack of infrastructure and landscaping elements, potential recreational facilities are not particularly popular with the population. The assessment of the stability of plantings determines their ability to withstand negative external influences affecting the growth and development of plants, leading to premature decay of stands and deformation of the species composition (Fig 6).
The estimated indicators of resistance to recreational effects adopted in the study correlate with the external signs of determining the stability of plantings during taxation
(Moiseev et al., 1990). The studied forest park plantings according to the scale of plantings stability
(Moiseev et al., 1990) belong to the 1
st and 2
nd classes. Healthy coniferous trees in plantings are noted from 71% to 90%, deciduous - at least 60%. Viable, reliable undergrowth and brushwood are noted in the plantings (Fig 7). The ground cover is mainly alive. At both sites in coniferous tracts, a moss cover is detected.
The predominance of annual weed species, as the main criterion of digression in arid zones (
Solodovnikov and Kanishchev, 2012), is noted mainly in areas bordering transport highways, as well as on the territory of the Kamyshin’s Arboretum (sections 1 and 4). In general, the satisfactory condition of the plantings is noted.
The results obtained allow us to draw an objective picture of the state of the objects under study to assess the prospects and consequences of further recreational use (Fig 8). The average attractiveness scores for both objects range from 1.03 to 2 points. The lowest score (1.03) is the indicator of horizontal density of plantings on the territory of the complex in the city of Kamyshin due to the large number of open spaces. The highest values at both sites are indices of tree stand age and vertical density (1.89/2 and 1.5/1.86 - Kamyshin/Volgograd, respectively). High ratings of the comfort indicator at the facilities are provided by the calm terrain (1.9/2) and the presence of a sufficient number of shaded areas (1.17/1.17). At the same time, both sites lack infrastructure and landscaping elements (0/0), as well as recreational reservoirs (0/0). Relatively comfortable noise conditions are provided in areas with high tree stands (1.77/1.14). The indicator of sustainability of plantings is one of the most important for measures of positive selection of trees for protective afforestation and landscaping. A comprehensive assessment of the indicator of 0.39 points for plantings in Kamyshin was formed due to the differentiation of types of plantings. The forest park complex in Volgograd shows greater stability - 0.5 points. The indicators of recreational impairment (1.14) and the presence of undergrowth (1.57) have high values.
Based on the results obtained, it was concluded that the recreational potential of the studied territories can be assessed as sufficiently high. Thus, of the total number of plantings of the Lapshin Garden forest park, most,
i.e. 63% of the territory, belongs to the II class of recreational value (CRV) (Fig 9a) and 37% of the territory belongs to the III CRV. Plantings on the territory of the Kamyshin forest area were also divided into two classes: 67% - II CRV and 33% - III CRV (Fig 9b).