Digital Technology Promotes Innovation in Landscape Architecture Design Concepts and Practices
Pubblicato online: 29 set 2025
Ricevuto: 06 gen 2025
Accettato: 19 apr 2025
DOI: https://doi.org/10.2478/amns-2025-1092
Parole chiave
© 2025 Ye Sun and Mingming Chen, published by Sciendo.
This work is licensed under the Creative Commons Attribution 4.0 International License.
Landscape garden design is an important part of modern urban planning and environmental construction, and the innovation of its design concept is of great significance for creating livable, beautiful and ecological urban environment [1]. Landscape garden and landscape design has existed since ancient times, but with the development of computer technology, drawing software such as Autocad, Photoshop, 3Dsmax and so on have been researched, which has led to the design of landscape garden and landscape with the characteristics of systematic, comprehensive, real, reasonable, beautiful, precise, efficient and easy to modify [2-4]. However, with the development of society, based on the new ecological civilization and information technology requirements, the landscape garden planning industry, which has covered the construction of urban ecological areas and infrastructure, has made urban landscape garden planning increasingly difficult [5-7]. For this reason, digital landscape garden landscape planning is proposed, using computer arithmetic and graphic capabilities, analyzing the spatial environment of the landscape garden landscape planning area, rationally constructing an objective and rigorous design logic, so that the landscape garden landscape has both scientific, artistic and social values [8-11].
In the digital assisted design of landscape garden, it can intelligently analyze the site, conditions, etc., so that the arithmetic results are more accurate. On the one hand, through the use of intelligent terminal mobile devices, designers can make supplementary changes to their own planning and design drawings at any time, so that they are free from the constraints of location, time, energy and other factors, to realize the “digital mobile office” [12-13]. On the other hand, it can also effectively save the design drawings, reduce unnecessary paper waste, to meet the overall design needs [14]. In addition, the use of computer-aided mapping, will effectively ensure that its overall design and planning is more scientific and logical, so that it can be effectively detached from the past in the garden design rely on the overall planning and design of the art of creation, to avoid the overall limitations, so that it can be effectively developed, balancing the science as well as artistry embedded in the landscape garden [15-17]. In conclusion, the landscape garden design under digital technology support can effectively change the two-dimensional plane construction drawings, simplify the construction pathway, by virtue of the digital model and the database, the overall construction becomes more efficient, accurate, and has important practical value [18-19].
This paper constructs a landscape garden routing design model based on ant colony Dijkstra combinatorial algorithm. A dijkstra shortest path planning algorithm based on swarm optimization is proposed to first create an environment map based on the landscape garden field. Then the dijkstra shortest path algorithm is improved by using ant colony optimization, and the fitness function is re-modified in order to make individuals with high fitness easier to be selected. Then the pheromone concentration updating method is proposed. The model is completed and compared with the baseline model on the dataset and analyzed in a mountain park landscape design case.
Paradigm and model together constitute the basis for interpreting the mechanism of parametric landscape planning and design, which are interpreted from the theoretical and technical levels respectively. Corresponding to the interweaving of sensibility and rationality in landscape garden planning and design, the alternation of qualitative and quantitative methods acts in the whole process of parameterized landscape garden planning and design. From paradigm to model, the process from law interpretation to form generation is revealed layer by layer. The mechanism of parameterized landscape garden planning and design is shown in Figure 1.

Parametric landscape land scape planning design mechanism diagram
From a metaphysical point of view, paradigm and model are a methodological presentation, which is neither a typical and targeted method nor a specific path and strategy: from a metaphysical point of view, paradigm and model can guide the way and method of generating design. From this point of view, the research on the mechanism of parameterized landscape garden planning and design has a high degree of methodology, but also comes from the design practice, and will ultimately guide the design practice.
A parameter can be a constant value assigned to a given application, and in a generalized sense, a variable used to control other quantities that change in response to its change, but it differs from the conceptual variable in that a parameter defines the operational characteristics of a system and the interrelationships between the system’s constituent elements.
Thus, parameterization is essentially a term describing a process, referring to a specific relationship established between variables, where a change in the factors of one variable causes a change in the parameters of the other variables while the specific relationship it defines remains unchanged.
Parametric design method in architecture refers to the fact that various influencing factors such as external influences and internal requirements of a building are regarded as covariates, and according to the design problem, the architect finds the rules for linking each covariate, selects appropriate design entry factors, constructs design prototypes expressed by parametric models, and automatically generates a large number of different design solutions by computers through the different parameter combinations and automatically compares these design solutions according to the computer performance evaluation index corresponding to the design entry factors. According to the computer performance evaluation index corresponding to the design entry factors, these design solutions are automatically selected, and when the design goal is reached or the design resources are exhausted, the architect selects the final design result from the many optimized design solutions [20].
Here, the parametric design method mainly includes four parts: performance evaluation, parametric modeling, scheme generation and machine intelligence and its termination conditions. Since the scale of concern, the materials involved, the structure and the problems to be solved and faced are quite different between landscape architecture and architecture, the parametric planning and design methods in landscape architecture cannot be completely copied directly in architecture, but can only be used as a reference and borrowed.
There are two research directions for the parameterized planning and design method of landscape garden, one is still using the traditional planning and design method, but the “parameterized software” as its auxiliary tool, similar to AUTOCAD, PHOTOSHOP and other software, auxiliary drawing, but not auxiliary design, which is stuck in the technical level. The other is the method respected in this paper, it is through the climate, terrain, water, soil, plants, space, economy and other factors data, relying on the establishment of parametric relationships, the construction of the landscape system, through the analysis of the design of the factors affecting the analysis of the design of the data, to get some meaningful information data, these information data for classification, screening, set specific rules, the establishment of parametric relationships, after continuous debugging to get a site-adaptive debugging to get the design result with site adaptability.
The advantages of parametric planning and design methods over traditional planning and design methods are mainly reflected in the characteristics of parametric thinking, that is, the difference between linear thinking and nonlinear thinking, it can be said that linear thinking is a kind of straight line, unidirectional, lack of change in the way of thinking, nonlinear thinking overcomes the defects of its simplicity, reductio ad absurdum, mechanical, and it is a kind of interconnected, discontinuous, uncertain, unpredictable and complex Thinking mode. The “parameterization method” under the influence of non-linear thinking has the characteristics of wholeness, correlation, process and place.
Holistic. The world is an indivisible whole, any landscape as part of the world, its own and with the surrounding environment is a unified organism. Relevance. Things are not isolated, but by a variety of potential factors originate, the results of the manifestation of these intricate factors random flow of change, mutual influence to generate entities. Process. The process of parametric approach is mainly reflected in the landscape as a dynamic system, and is not limited to spatial thinking and static structural analysis. Place-based. Parametric planning and design method is to respect nature, respect the place of generative design methods, it is in varying degrees with China’s classical gardens, “unity of man and heaven”, “although made by man, just like the sky from the beginning” and other ideas like the same.
Since parametric methods are used throughout the whole life cycle of landscape planning and design, with different focuses at different work stages, there are many kinds of parametric software, such as Weather Tool, CFD analysis tool, Virtual Design Builder, Grasshopper, Rhino, Digital Project, Forms, GC, etc. Here we mainly introduce the Geographic Information System (GIS) software used in the investigation and analysis phase and the Building Information Modeling (BIM) tool throughout, as well as the Vectorworks software that is used more in Europe, America, and Japan, to roughly understand its functions and applications, and to pave the way for the understanding of the following parameterized methods in the whole life cycle of landscape architecture specific applications.
The steps of GIS application in the investigation and analysis phase of landscape planning and design can be summarized as the following six points, which are: 1) establishing the initial problem; 2) acquiring the appropriate software or plug-in platform; 3) collecting and acquiring the relevant data; 4) establishing the database; 5) calculating, analyzing, and processing the data in the database; and 6) interpreting and presenting the results in the form of tables, graphs, and images. GIS is combined with Civil3d and Autocad, i.e., it constitutes the data management center of the whole parametric planning and design [21].
BIM is to take all the relevant information data of the construction project (including all the research information, design, materials, data statistics, cost, etc.) as the basic platform.
Using BIM building information modeling, the data of all parts of the project can be placed in the same information model at the same time, which is convenient for designers to design and modify the program; all professionals communicate on the same platform, which enhances cooperation and coordination and reduces the amount of rework; BIM technology can be used in the whole life cycle, which allows for planning in advance of the project expectations, schedule control, budget, etc., which reduces errors and omissions, and improves the quality of the drawings.
BIM contains two levels: information modeling and information management. At the level of information modeling, it is a model with a database containing three kinds of information: model elements, view elements and annotation elements.
In the landscape model, the model element is the digital simulation of landscape entity elements, including terrain, garden road, plants, paving, landscape sketches and facilities, etc.; the view element is the expression of the digital simulation of landscape entity, i.e., flat elevation section, perspective view and bird’s-eye view, which is connected with the model element, and can be modified synchronously.
Taking the planning of some areas in a provincial capital hill landscape area as an example, the map of landscape environment is constructed with the size of 5000m×5000m rectangle, in which the black polygons indicate the different attraction areas in the landscape area, which are regarded as obstacle areas
Assuming that the landscape environment is
where
Where:
The research direction chosen in this paper is the road routing model for landscape planning based on path distance algorithm. At present, the most typical shortest path algorithm is Dijkstra’s algorithm, and this algorithm is used to solve the single-source shortest path problem. Therefore, after setting source
The dijkstra shortest path algorithm is improved by using swarm intelligence algorithm, the specific swarm intelligence algorithm is a typical ant colony algorithm. The initial path obtained based on Dijkstra’s algorithm is used as the initial value of the ant colony algorithm for optimization [23]. Let points
Then, the length of the path from source
Different combinations of
Where
The ant search is adjusted as:
where
Repeat the above procedure until the maximum number of iterations allowed, or all ants obtain a unique element, i.e., the optimized
With the change of time, the exploration process of ant colony will be accompanied by the volatilization of pheromone, so it is necessary to reasonably update the pheromone information on the path, in which the local pheromone update rule is:
Where:
where
The effectiveness of the Ant Colony Dijkstra Combinatorial Algorithm is generally affected by the pheromone α, the heuristic factor β, and the degree of increase or decrease in the number of visits to the updated landscape ρ. In order to test the effectiveness and superiority of the algorithm, the dataset of TSPLIB95 is selected, and the simulation is carried out in Matlab2023 software environment under the conditions of α=1.6, β=4, ρ=0.6, and the initial value of pheromone Q=500 with 250 iterations of repetition.
Figure 2 shows the classical ant colony algorithm route planning curve, the shortest path is 515.24 m. Figure 3 shows the classical ant colony fitness curve, the best iteration 182 times convergence; Figure 4 shows the ant colony improved Dijkstra algorithm route planning curve, the shortest path is 304.78 m. Figure 5 shows the ant colony improved Dijkstra algorithm fitness optimization curve, the best iteration 69 times convergence. It can be seen that the ant colony improved Dijkstra algorithm in this paper reduces the number of iterations, avoids a large number of blind iterations, reduces the adjustment of parameters, and improves the time efficiency and optimization performance of the algorithm. Generating the optimal population can accelerate the speed of Dijkstra and avoid the problem of falling into the local optimum in the solution process, thus obtaining the optimal solution.

Path planning curve of classical ant colony algorithm

Fitness curve of classical ant colony algorithm

Path planning curve of improved ant colony algorithm

Fitness curve of improved ant colony algorithm
By importing the dataset of TSPLIB95, increasing the amount of pheromone α, maintaining the heuristic factor β and the degree of increase or decrease in the number of visits to the updating landscape ρ unchanged, i.e., repeating the iteration of the three algorithms for 250 times under the conditions of α=3, β=4, ρ=0.6, and Q=500, respectively, and the results of the experiments are shown in Table 1.
Comparison of route planning effects among algorithms
Algorithm type | Path length/m | |
---|---|---|
GA | 572.85 | 196 |
Dijkstra | 529.21 | 202 |
This model | 275.37 | 81 |
The results show that the ant colony improved Dijkstra’s algorithm for route planning has reduced repetition rate, fast convergence speed, and the planned path length is significantly shorter than that of GA and Dijkstra’s algorithm.
The improved ant colony Dijkstra’s algorithm is applied to the problem of clustering landscape planning data in landscape gardens to obtain better results.
This paper takes a local mountain ecological park as an example, and applies the proposed landscape routing design model to evaluate and discuss the landscape quality and recreational service capacity of the mountain ecological park in the urban center of the city through the parameterized software using GIS as an example, so as to provide a reference for the enhancement of the quality of the recreational environment in the local urban public space, and to provide an important scientific basis for the construction of the public space.
After consulting with 30 gardening and ecological experts and reviewing relevant literature, 29 evaluation indicators closely related to the recreational services of Lanshan Mountain Ecological Park were finally screened and identified, namely:
Plant species richness, green coverage area, species diversity, completeness of ecological elements, landscape ecological sustainability, water body area, plant landscape level and color change, diversity of ornamental characteristics, terrain and geomorphology richness, terrain space coordination/utilization rate, coordination between the water body and the surrounding landscape/park environment, harmony between plants and hardscape, hydrophilicity of the water body, richness and coordination of landscape elements, road density The above 29 factors are categorized into ecological and landscape factors, such as the spatial coordination/utilization of landscape, harmony between plants and hardscape, hydrophilicity of water body, richness and coordination of landscape elements, road density, accessibility to scenic spots, distance to water body, security/privacy of landscape space, comfort of landscape scale, percentage of area for recreation and viewing activities, area occupied by per capita, interaction between human beings and landscape, completeness of scenic spots’ facilities, recreation and sports facilities, service and leisure facilities, spatial layout for recreation and leisure services, completeness of infrastructures, facilities for culture, education and propaganda, disaster prevention and evacuation.
The above 29 factors are divided into 4 aspects, namely, ecological benefits, aesthetic experience, behavioral feelings, and social functions, and the framework of the evaluation system of the recreation service capacity of mountain parks is constructed in this way, as shown in Table 2.
Evaluation system of landscape quality and recreation service capacity
Natural landscape quality | Ecological benefit | Greening | Species richness |
Green coverage product | |||
Species diversity | |||
Landscape ecology | Ecological factor completeness | ||
Landscape ecological sustainability | |||
Water area | |||
Aesthetic experience | Landscape visual attraction | Landscape level and color change | |
Ornamental diversity | |||
Landscape beauty | Landform richness | ||
Terrain space coordination/utilization | |||
The environment coordination of the surrounding landscape/park | |||
Plants and hard landscape harmony | |||
Landscape experience | Hydrophilic water | ||
The landscape elements are rich in coordination | |||
Human landscape quality | Behavior feeling | Accessibility | Road density |
Scenic accessibility | |||
Reach of water | |||
Landscape comfort | Landscape space security/privacy | ||
Landscape dimension comfort | |||
The activity surface product ratio | |||
Per capita area | |||
Interactivity | People and landscape interactivity | ||
Accessibility | Completeness of scenic spot | ||
Social function | Service function | Recreational facilities | |
Service lounge | |||
Leisure service space layout | |||
Consumability of infrastructure | |||
Education function | Cultural education publicity facilities | ||
Emergency escape function | Disaster prevention |
The four aspects of ecological benefits, aesthetic experience, behavioral feelings, and social functions were used as the guideline layer to derive the landscape evaluation weight values. Subsequently, the landscape experts were invited to compare the indicators, and the weight values of each indicator were finally obtained by constructing judgment matrices A-B, B1-(C1-C6), B2-(C7-C14), B3-(C15-C23), and B4-(C24-C29). The final weights are shown in Table 3.
Landscape evaluation weight table of Mountain Ecological Park
Target layer (A) | Standard layer (B) | Weight | Factor layer © | Weight |
---|---|---|---|---|
Landscape evaluation of mountain ecological park | B1 | 0.344 | C1 | 0.051 |
C2 | 0.084 | |||
C3 | 0.037 | |||
C4 | 0.056 | |||
C5 | 0.081 | |||
C6 | 0.035 | |||
B2 | 0.197 | C7 | 0.047 | |
C8 | 0.039 | |||
C9 | 0.028 | |||
C10 | 0.024 | |||
C11 | 0.017 | |||
C12 | 0.014 | |||
C13 | 0.014 | |||
C14 | 0.014 | |||
B3 | 0.257 | C15 | 0.016 | |
C16 | 0.051 | |||
C17 | 0.044 | |||
C18 | 0.041 | |||
C19 | 0.032 | |||
C20 | 0.013 | |||
C21 | 0.025 | |||
C22 | 0.021 | |||
C23 | 0.014 | |||
B4 | 0.202 | C24 | 0.013 | |
C25 | 0.044 | |||
C26 | 0.022 | |||
C27 | 0.039 | |||
C28 | 0.051 | |||
C29 | 0.033 |
A total of 145 questionnaires were distributed to three groups of people in the investigated mountain ecological parks, namely, park staff, park residents and tourists, who were looking for a better understanding of the scenic environment, and were invited to evaluate and communicate one-on-one with each other about the landscape quality and recreational service capacity of the Lanshan Mountain Ecological Park under the parametric design method based on GIS, and ultimately scored on the spot. Five satisfaction scoring criteria were set for 29 factors related to landscape, with 1-2 being very dissatisfied, 3-4 being dissatisfied, 5-6 being basically satisfied, 7-8 being relatively satisfied, and 9-10 being very satisfied. A total of 142 questionnaires were collected, and the recovery rate and validity rate were 97.93%.
According to the fuzzy evaluation method to derive the average score of each factor after the use of comprehensive evaluation method to find the park guidelines layer B score as well as the final score of the park, the results are shown in Table 4.
Landscape score statistics of Mountain Ecological Park
Total score:7.36 | Ecological benefit | 2.58 | C1 | 7.95 |
C2 | 8.06 | |||
C3 | 6.83 | |||
C4 | 6.43 | |||
C5 | 7.88 | |||
C6 | 7.16 | |||
Aesthetic experience | 1.42 | C7 | 6.29 | |
C8 | 8.35 | |||
C9 | 7.05 | |||
C10 | 7.9 | |||
C11 | 5.95 | |||
C12 | 7.53 | |||
C13 | 6.02 | |||
C14 | 8.34 | |||
Behavior feeling | 2.01 | C15 | 7.37 | |
C16 | 8.65 | |||
C17 | 8.04 | |||
C18 | 8.15 | |||
C19 | 7.33 | |||
C20 | 7.94 | |||
C21 | 7.94 | |||
C22 | 6.74 | |||
C23 | 5.96 | |||
Social function | 1.35 | C24 | 5.09 | |
C25 | 5.51 | |||
C26 | 6.95 | |||
C27 | 6.34 | |||
C28 | 8.09 | |||
C29 | 6.84 |
Among the indicators in the factor layer, the highest score is C16 Scenic landscape accessibility, which is 8.65 points. This was followed by C8 Diversity of ornamental features and C14 Richness and coordination of landscape elements with 8.35 and 8.34 points respectively. The final total score is 7.36, which is at a relatively satisfactory level.
The statistical map of the landscape factor layer scores of the mapped mountain ecological parks is shown in Figure 6.

Factor level C score statistics of park
The classification statistics of the scores of each factor included in the four guideline layers of ecological benefits, aesthetic experience, behavioral feelings, and social functions are shown in Figures 7 to 10, respectively.

Ecological benefit score classification chart

Statistical chart of the aesthetic experience score

Behavioral sensory score classification chart

Social function score classification chart
As can be seen from Figure 7, in terms of ecological benefits, the richness of plant species, green coverage area, landscape ecological sustainability and other aspects of the parametric design scored higher, respectively, 7.95, 8.06, 7.88, indicating that the parametric design of the landscape ecological aspects of the landscape planning is better, through the analysis of the solar radiation obtained by the GIS, topography and geomorphology analysis, hydrological analysis, the current situation of the vegetation analysis carried out after the Reasonable plant selection and collocation to create a good landscape ecology, rich plant species, reasonable plant level collocation, high green coverage, birdsong and flowers hard open space, the use of energy-saving materials and reasonable ecological design techniques all add color to the park.
In terms of behavioral feelings, Figure 9 shows that the parametric design scores higher in terms of accessibility to attractions, distance to water bodies, and security/privacy of landscape space, respectively 8.65, 8.04, and 8.15, indicating that the rationality of the road network layout and distribution of attractions analyzed by the parametric software is generally accepted, and that behavioral feelings are an important criterion layer element for landscape evaluation, and the security/privacy of landscape space includes many aspects. The safety/privacy of landscape space includes many aspects, such as the safety of park greening, road network design, paving, landscape sketches and facilities, water bodies, etc., and the comfort brought to people through the rational layout of landscape space is higher.
The aesthetic effect of the park should pay more attention to the integration of park landscape and urban landscape style. Figure 8 in the parametric design in the diversity of ornamental characteristics, landscape elements rich coordination and other aspects of the landscape score is more leading, respectively, 8.35, 8.34, indicating that the parametric design for the aesthetic experience of this level also has a certain degree of optimization and enhancement, should be more consideration of the level of plant collocation, species selection, ornamental characteristics, landscape spatial layout, as well as landscape elements of the completeness, richness of the coordination, etc., to meet the visual needs of visitors. Visitors’ visual needs.
At the level of social function, Figure 10 clearly shows that parametric design generally scores low, indicating that the optimization and improvement of parametric design at this level is not great. Recreation and sports service facilities and service leisure facilities score 5.09, 5.51, parametric design in the social function level is not perfect, all kinds of infrastructure is not complete, can not meet the needs of tourists, although there are sanitation, leisure facilities, park management office, parking lot, these basic settings, but the park lighting, communication facilities, signage and other indicative service facilities, as well as some recreational and fitness facilities are not involved. In this regard, more reference should be made to the setting and layout of recreational and service facilities in various parks.
In this paper, we design the ant colony Dijkstra combinatorial algorithm to construct a landscape routing design model. Simulation experiments are carried out on the dataset to analyze the optimization performance of the combined algorithm, and a mountain park is used as an example to apply the proposed scenic routing design model to analyze the landscape quality and recreational service capacity. It is found that the classical ant colony algorithm route planning curve, the shortest path is 515.24 m, and 182 iterations converge. In this paper, the shortest path of ACO Dijkstra’s algorithm is 304.78 m, which converges and stabilizes in 69 iterations. Parametric design provides ideas for landscape garden design in terms of ecological benefits and visitor perception, and the mountain ecological park designed by this model brings better comfort and experience to visitors in terms of road network arrangement and attraction distribution, but its effect in terms of social function is unsatisfactory, and the aesthetic sense needs to be improved.