J Navig Port Res > Volume 48(5); 2024 > Article
Kim, Lee, Ahn, and Lee: A Study on The Suitability Assessment of a Coastal Maritime Transportation Network Considering Spatio-Temporal Operational and Environmental Characteristics

ABSTRACT

Recently, various marine development initiatives, including offshore wind farms and marina port facilities, have been launched to enhance utilization of coastal waters. In addition, advancements in technologies for autonomous ships and wing-in-ground effect craft are progressing swiftly, increasing the complexity of maritime traffic. Accordingly, proactive policy development and research are needed to ensure safe navigation and decrease maritime accidents. The dynamic interplay between vessel traffic and geographical features in coastal waters necessitates spatio-temporal analysis. Factors such as currents, waves, and fog, along with vessel traffic services, play pivotal roles in managing maritime traffic. In this study, AIS data were used to quantitatively evaluate the distribution and utilization of maritime traffic in coastal waters using a grid cell approach. Furthermore, a suitability model for maritime traffic routes was developed, taking into account spatio-temporal operational and environmental characteristics. Results were compared to existing national maritime traffic route and offshore wind farm plans, providing valuable insights for the development of future maritime traffic networks.

1. Introduction

In response to the demand for marine space utilization and changes in the development environment, countries, including Korea, are establishing marine spatial plans tailored to their national circumstances and are designating marine use zones for management (Chae, 2009). In Korea, under the 2019 Marine Spatial Planning policy, unrestricted use and development activities across the country’s waters were limited. Nine types of marine use zones were established based on a comprehensive assessment of the marine ecosystem's value and the development potential of these spaces. These zones ensure that marine areas are used and developed in accordance with their specific characteristics. The marine use zone designated to prioritize the safe navigation of vessels is referred to as the Port and Navigation Zone. However, as of 2019, most of the designated and managed Port and Navigation Zones cover only about 4.3% of the total territorial sea area, which is quite limited, and their locations are confined to currently designated navigation routes or waters within port boundaries. Belgium established a marine spatial plan in 2020, designating zones for seven sectors, including biology, energy, ports, fisheries, and defense. The port zones are designed to maintain a safe distance from energy zones, such as offshore wind farms, to ensure vessel safety. Germany introduced a similar plan in 2021, designating zones for eight sectors, such as navigation, wind energy, and fisheries. Navigation and wind energy zones, in particular, are divided into core zones, buffer zones for safety, provisional zones for future development, and conditional zones for further demand analysis.
The maritime traffic environment in coastal waters is expected to become more complex due to future marine development plans (such as offshore wind farms) and new vessel operations, such as autonomous ships. As a result, proactive efforts, including policy development and detailed research, are needed to address changes in navigation, ensure vessel safety, and reduce maritime accident risks. In relation to government policies for establishing maritime traffic networks, the first step to ensuring safe navigation routes is to thoroughly review the distribution of vessel traffic and navigational conditions in domestic coastal waters (OPNT, 2024). This will allow for a detailed understanding of the maritime traffic characteristics in each area, which will serve as the foundation for setting up appropriate maritime traffic routes (Kim, 2021; Yoo et al., 2019).
When constructing infrastructure, such as offshore wind farms, in coastal waters, it is crucial to understand maritime traffic characteristics during the site selection process, to avoid overlapping with major traffic routes or high-density areas, thereby ensuring unobstructed maritime traffic flow.
There are numerous case studies on securing foundational data, such as assessing the adequacy of maritime traffic systems, through quantitative analysis of current traffic volume, maritime traffic patterns, and density based on AIS data. However, an appropriate evaluation model is lacking for selecting suitable sites for maritime traffic routes and offshore wind farms, as well as for planning maritime area utilization, such as visualized data by grade based on vessel traffic distribution and maritime traffic utilization levels by area. In particular, when conducting GIS-based vessel density analysis, it is possible to overlay, visualize, map, and extract maritime traffic information using vessel trajectory data. However, limitations arise due to variations in accuracy based on the density analysis method used, such as point, transit, or line density, and due to the effects of vessel speed and cell size settings. Additionally, discrepancies with the actual navigation environment may occur due to the influence of vessel size. Therefore, this study aims to develop and evaluate a suitability assessment model for maritime traffic routes that considers the spatio-temporal navigational environment characteristics of coastal waters. Based on the current maritime traffic conditions in Korea, this model seeks to establish optimal maritime traffic routes that ensure safe vessel navigation and support the efficient planning of coastal area utilization.
The study focuses on the complex interaction between vessel characteristics and geographical features in coastal waters, highlighting the importance of spatio-temporal analysis for assessing maritime traffic conditions. It identifies three main objectives:
1. To establish optimal maritime traffic routes by collecting detailed data on vessel types, Length Overall (LOA), Speed Over Ground (SOG), and vessel transit frequencies, as well as environmental factors such as currents and waves.
2. To assess traffic routes and congested areas in advance to aid in site selection and the effective use of maritime areas, particularly for infrastructure, such as offshore wind farms and marinas.
3. To input spatio-temporal operational and environ -mental characteristics into a suitability evaluation model, allowing for a visual representation of maritime traffic utilization levels based on user requirements.

2. Literature Review

The Automatic Identification System (AIS) data transmitted and received by ship AIS equipment consists of static information, including the ship's name, call sign, IMO number, Maritime Mobile Service Identity (MMSI) number, and ship type; dynamic information, including the ship's position (longitude/latitude), speed, and course over a period of time; and navigational information, including the ship's draft and cargo information (Hwang et al. 2016). Accordingly, AIS data is utilized as essential information in various studies related to the analysis of maritime traffic conditions in target sea areas, such as ports and shipping routes, both domestically and globally. Since 2020, the Korean government has been conducting safety assessments of ship routes based on AIS data to develop a systematic maritime traffic network. As a result, maritime traffic routes have been proposed according to the characteristics and intended uses of domestic maritime traffic, providing foundational data for establishing and implementing various policies for maritime traffic network construction and operation (Kim et al., 2020; Cho et al., 2023). The study has utilized AIS data collected over four seasons from Korea's coastal waters to extract maritime traffic routes and identify networks, through a quantitative big data analysis. This study also extracted traditional maritime traffic flow based on the top 25% of ship density (Kim et al., 2022). Another case included comparing and reviewing changes in navigators' risk levels resulting from increased maritime traffic and route width, using the Environment Stress (ES) Model, a risk assessment model, based on AIS data from the waters near Gunsan Port (Kang et al., 2022). Additionally, a case study that used AIS data from the waters near Mokpo Port performed a comparative analysis of the spatial flow of maritime traffic and the traffic network by time of passage (Oh et al., 2020). There is also a case where the DBSCAN algorithm, a machine learning clustering method, was used to analyze ship traffic patterns based on AIS data from the waters near Busan New Port. This study derived and presented the range of changes in ship positions, speeds, and courses over a designated time series (Lee et al., 2021).
Internationally, studies have been conducted that have investigated the complexity and spatial distribution of target sea areas using AIS data from ships in China (including Shenzhen) and Singapore. These studies designed methods for estimating both ship traffic volume and maritime traffic complexity models that reflect ship characteristics and the speed of ships in accident-prone sea areas (Wen et al., 2015; Liye et al., 2019).
Spatiotemporal pattern analysis is a type of Exploratory Spatial Data Analysis (ESDA) and serves as a useful method for identifying characteristics from large amounts of spatial data (KRIHS, 2011). Many phenomena tend to be distributed around specific locations in a given space, and these characteristics appear as distinct spatial patterns. This is called spatial autocorrelation, and it has been applied in cases such as preventing the spread of infectious diseases or preventing crime.
In Korea, after the Hebei Spirit oil spill incident in December 2007, researchers conducted an analysis on the spatiotemporal change patterns of oil pollution near the waters of Mallipo to assess and forecast the progression of the oil contamination. The study presented results that compared the temporal and spatial change patterns of oil concentrations. Over the course of four years, the rate of decrease in oil concentration during the winter was twice as fast as in the summer throughout the Mallipo area (Kim, 2012). Meanwhile, although point, line, and area-based spatial data have been available for some time, research using a grid system is essential for understanding the accuracy, characteristics, and trends based on a certain scale, as well as advancing related studies and establishing policies. Accordingly, a proposal for a national grid system for an integrated national grid data management system was presented, which included the format and methods for providing grid data (Kim et al., 2015). Additionally, to consider the burden on navigators in different sea areas, Korea's coastal waters have been divided into eight regions, and key evaluation criteria (average number of foggy days, route complexity, maritime traffic volume, and hazardous cargo handling amount) were established. A case study also evaluated the safety of ship traffic using Fuzzy Logic and the Choquet integral method (Keum et al., 2006). In one case, the waters near Busan Port were divided into a grid with 6-minute latitude and longitude intervals, and a Marine Traffic Risk Index model was proposed, which calculated risk indices by synthesizing risk indicators, evaluation criteria, and weighting factors (Park, 2021). Internationally, a study analyzed the temporal and spatial evolution of ship traffic and types in the Canadian Arctic between 1990 and 2015. The study presented patterns and trends in its findings and proposed them as foundational data for policy decisions regarding the development of maritime transportation across the Arctic (ARCTIC, 2009).

3. Methodology

3.1 AIS Data Analysis

This study conducted an analysis using AIS data from all vessels passing through Korean coastal waters. The SOG and COG are represented as continuous values according to the reception time, and the AIS data is provided in the latitude and longitude coordinates of the WGS-84 geodetic system. However, a consistent time unit must be used for each vessel because the reception cycles for dynamic information vary depending on the vessel's speed, ranging from 2 seconds to 3 minutes. To address this, missing values must be processed. Therefore, during the preprocessing stage of the AIS data, missing values for critical data such as LOA, SOG, and transit frequency were managed based on MMSI from the dynamic data. Linear interpolation, as illustrated in equation (1), was used to process the missing values (Lee et al., 2021).
(1)
D(t+Itv)=l1lD(t)-l2lD(t+α)
where D(t)=data at time t; D(t+a)=data after time a (next data of D(t)); D(t+Itv) =data after interval to be interpolated; l, l1, l2=difference between D(t) and D(t+a), D(t) and D(t+Itv), D(t+Itv) and D(t+a), respectively; Here, the prerequisite is a > Itv.
Next, by referencing the horizontal grid system operated by the Korea Hydrographic and Oceanographic Agency (KHOA), the grid-cell type was modeled, and spatio-temporal characteristics, such as LOA, SOG, and transit frequency, for each ship type were analyzed.
The data utilization flowchart, including the processes of collection, processing, and analysis of ship AIS data, is shown in Fig. 1.
To understand the characteristics of ships navigating through domestic coastal waters through modeling of spatio-temporal operational and environmental analysis, the AIS data analysis period and scope were defined as follows. The analysis period was set to three days per season (a total of 12 days), to align with the previous coastal waters maritime traffic survey. For the analysis scope, the latitude 032°∼040°N and longitude 124°∼132°E range was used to encompass the main maritime traffic flows within the domestic coastal waters.

3.2 Suitability Assessment Overview

In this study, we sought to analyze the spatio-temporal operational environment characteristics based on a grid-cell type framework by using AIS data. Accordingly, we designed a Suitability Assessment Model of Maritime Routes (SAMR) to establish optimized maritime traffic routes for the current state of domestic maritime traffic and to promote efficiency and cost-effectiveness in the use of coastal waters. The design outline is presented in Fig. 2.
To develop a maritime traffic route suitability assessment model, we quantitatively analyzed the distribution of LOA, SOG, and transit frequency according to ship type in domestic coastal waters. Since these spatio-temporal characteristics are crucial for the model, they need to be considered comprehensively. Thus, we defined the Maritime Traffic Sensitivity Index (MTSI) using the mean values of LOA, SOG, and transit frequency, as illustrated in equation (2). The MTSI reflects the maritime traffic utilization level, which can be compared across different areas to understand relative traffic levels (Kim, 2024).
(2)
MTSI=1ni=1nSi
where Si is an index of analysis items that can be expressed as S1, S2, and S3; S1 is the level that includes the average LOA for each grid-cell type; S2 is the level that includes the average SOG for each grid-cell type; S3 is the level that includes the maximum transit frequency for each grid-cell type; n is the number of analysis items for the distribution of transit ships (n = 3)
The MTSI, which comprehensively considers the spatio-temporal characteristics of ships operating in domestic coastal waters, is divided into 10 levels according to the maritime traffic utilization level, as shown in Fig. 3. MTSI Level 1 indicates a very low level of maritime traffic utilization, with smaller, slower, and less frequent ships. MTSI Level 10 represents a very high level of maritime traffic utilization, with larger, faster, and more frequent ships. Therefore, when constructing maritime traffic networks, Level 10 should be prioritized, while Level 1 is ideal for facility installations like offshore wind farms.
The range values for each MTSI level reflect the distribution of all ships based on the spatio-temporal analysis results, as shown in Table 2. These values are crucial input data for deriving the MTSI and can be adjusted based on the results of the spatio-temporal analysis. The values for each level were determined by applying an equal interval partitioning method to divide the entire dataset into 10 groups of equal size.
This study focuses on weather conditions like tidal currents, wave heights, and fog, as well as operational factors such as the Vessel Traffic Service (VTS) area to calculate and assign weights based on the spatio-temporal characteristics of each sea area (KCG, 2024). Additional factors can be included depending on the study's objectives and application. SAMR, which considers the spatio-temporal operational and environmental characteristics in domestic coastal waters, is expressed as the product of the MTSI, representing maritime traffic utilization levels, and the representative weight for each sea area. It is defined in equation (3).
(3)
SAMR=MTSI1ni=1nwi
where wi is an index of weight value items that can be expressed as w1, w2, w3 and w4; w1 is the weight calculation value based on tidal characteristics; w2 is the weight calculation value based on wave characteristics; w3 is the weight calculation value based on fog characteristics; w4 is the weight calculation value based on VTS area; n is the number of analysis items for the weight value (n = 4).
Designing maritime traffic routes based solely on areas with the highest aggregated values, while treating all spatial and temporal characteristics equally, may lead to generalization errors. Since each area has distinct spatio-temporal traits that impact traffic flow and volume differently, applying differentiated weights to key factors is recommended.
The weight items were divided into three groups based on their influence on the flow and volume of ship traffic. Since no specific quantitative criteria were defined, the ranges were determined through qualitative evaluations by senior researchers, based on input from maritime traffic experts and VTS operators. In the maritime route suitability model, low-impact items are represented as wlow and high-impact items as whigh, as shown in Table 3. The weight ranges were applied as follows: wlow is +5%, wmoderate is +15%, whigh is +25%. The comprehensive weight was calculated by averaging the sum of the weights for key items derived from each sea area.

4. Results and Discussion

To evaluate the maritime route suitability for different types of vessels throughout the domestic coastal waters, the distribution of ship length, speed, and transit frequency has been visualized for cargo ships (T1) and tankers (T2), which comprise a large proportion of the total AIS data and follow relatively conventional maritime traffic patterns. Additionally, based on the spatio-temporal analysis results, the maritime traffic utilization level for each sea area according to the MTSI, along with the results of the maritime route suitability assessment model, have been presented. In this study, the maritime traffic utilization levels based on the MTSI are presented as follows to interpret the analysis results from the maritime route suitability assessment model. Levels 1 to 5 indicate utilization from "Extremely Low" to "Low," while Levels 6 to 10 indicate "High" to "Extremely High."
In the case of T1, the analysis revealed that various patterns and segments with high maritime traffic utilization levels (SAMR Level 6-10) are present across the East, West, and South Seas, based on coastal navigation characteristics. For T2, the analysis showed that maritime traffic utilization levels are higher in the West and South Seas compared to the East Sea. From the analysis of maritime traffic utilization levels, it was determined that it is possible to identify optimal maritime routes and appropriate sea areas for facility installations. The analysis results using the maritime route suitability assessment model for T1 and T2 are presented in Table 4. The X and Y axes of the graph represent the number of grids.
The analysis results of maritime traffic utilization levels using the SAMR model on designated routes (Ongdo Fairway, N. Maemulsudo Fairway, S. Maemulsudo Fairway, and Hongdo Fairway), located in domestic coastal waters with a relatively large number of islands, complex coastlines, and active operations of vessels ranging from large to small, including fishing boats, are presented in Table 5. The X and Y axes of the graph represent the number of grids.
Most of the designated routes showed higher levels of maritime traffic utilization over a wider area for T1 compared to T2. However, the entry and exit sections of the Sindo Fairway, located near the Ongdo Fairway, showed higher maritime traffic utilization levels for T2 because of the frequent passage of hazardous cargo vessels, a characteristic of Daesan Port. The southern waters of Heuksando Island, located near the N. Maemulsudo Fairway, showed higher utilization levels for T1, as vessels travel offshore to areas such as China. Similarly, the southern waters of the Hongdo Fairway showed higher utilization levels for T1 because vessels move offshore from Busan and Ulsan Ports. Since 2020, the government has been conducting research into systematic maritime traffic network construction plans, considering the changes in ship traffic conditions due to the construction of various marine facilities (such as offshore wind farms) and the increased use of maritime spaces in domestic coastal waters, as well as the potential future use of coastal waters due to the development of autonomous ship technology. The primary research method involves employing computer algorithms and GIS programs based on the navigation environment and maritime traffic flow in domestic coastal waters (Son et al. 2019). This approach includes spatio-temporal density analysis and isodensity mapping for the spatial analysis of maritime routes, ultimately leading to the extraction of maritime route areas. Based on the characteristics and intended use of domestic maritime traffic, a total of four proposed maritime routes were derived, and the details are as follows. The wide area maritime route refers to the maritime traffic route which connects to the Traffic Separation Scheme (TSS) designated in the coastal waters of Korea, forming the main route with the highest traffic volume, circulating near the center of the country. The feeder maritime route and passenger ship maritime route refer to traffic routes for vessels using coastal and fishing ports, mainly used by ships navigating between islands and small harbors. The port access route refers to routes such as harbor entrances or legally designated routes, including those designated under the TSS.
The international navigation maritime route is located outside the main traffic routes. The results of overlaying the main maritime traffic routes on T1, showing varying levels of maritime traffic utilization across different sea areas, are shown in Table 6. The X and Y axes of the graph represent the number of grids. When deriving maritime traffic routes, priority was given to segments with high maritime traffic utilization levels (SAMR Level 6-10), considering the major maritime traffic patterns of each sea area.
The currently operating offshore wind farms and the planned construction sites are mostly located within the territorial waters of the West and South Seas or within the EEZ areas, and they appear to overlap with long-established conventional maritime traffic flows in domestic coastal waters. Based on the maritime traffic characteristics of T1, the suitability of maritime routes was evaluated by applying the MTSI and weights according to operational and environmental characteristics.
This evaluation was applied to the current offshore wind farm and wind measurement device locations to assess suitable sites, and the analysis results were detailed.
In the case of T1, a considerable number of segments with high maritime traffic utilization levels (SAMR Levels 6-10) in the East, West, and South Seas were found to overlap with the locations of offshore wind farms and wind measurement devices. In the East Sea, overlapping segments were identified in the waters connecting offshore areas such as Russia from Ulsan Port and Busan Port; in the West Sea, near Anmado; and in the South Sea, near Jindo and Chodo. A visualization comparing the current status of offshore wind farms and wind measurement devices with the results of the maritime route suitability assessment based on T1 is shown in Fig. 4. The X and Y axes of the graph represent the number of grids.
When installing offshore wind farms, it is important to plan transit or detour routes based on the SAMR results and to consider reducing the scale of the complex. Facilities should be restricted in areas with SAMR Levels 8 and above, and suitable locations should be reassessed.

5. Conclusion

In the case of domestic coastal waters, the characteristics of ships passing through these waters vary over time, and the geographic characteristics of each sea area also play a complex role. Therefore, spatio-temporal analysis is crucial for identifying the key maritime traffic characteristics of each area. Additionally, weather conditions such as tidal currents, waves, and fog, as well as operational environmental factors like VTS areas, significantly impact maritime traffic. Accordingly, each maritime route within the maritime traffic network must be designed with comprehensive consideration of both spatio-temporal operational and environmental characteristics to properly adapt to the conditions of domestic coastal waters.
This study analyzed spatio-temporal operational and environmental characteristics using ship AIS data and provided quantitative data on ship traffic distribution and utilization levels in the form of grid-based data. A SAMR incorporating the MTSI was developed. Furthermore, through the maritime route suitability assessment model, we established optimal maritime routes that ensure the safe navigation of ships and presented the validation and application results to enable efficient planning for the use of domestic coastal waters.
When using the maritime route suitability assessment model developed in this study based on AIS data, the maritime traffic utilization levels of each sea area, which comprehensively consider spatio-temporal and operational and environmental characteristics, can be visualized in a way that is easy for non-experts to understand. Additionally, it allows for the quantification of physical values reflecting the traffic characteristics of vessels in each sea area. In other words, the analysis results of ship traffic distribution and patterns by sea area based on AIS data enable the quantitative assessment of maritime traffic utilization levels in domestic coastal waters according to the MTSI. The grid-based data format is also efficient in terms of compatibility and connectivity with future studies.
Moreover, by using the maritime route suitability assessment model that considers spatio-temporal operational and environmental characteristics, it is possible to compare and verify proposed maritime route plans with offshore wind farm and wind measurement device installation plans. This will help establish optimal maritime routes that ensure the safe navigation of ships and contribute to efficient planning for the utilization of coastal waters.
Nevertheless, there are still limitations in this study. Since the results derived from the MTSI and SAMR are based on the distribution of vessel type, LOA, SOG, and transit frequency using AIS data from ships operating in domestic coastal waters, the analysis results are relative to the scope of domestic coastal waters. Therefore, if the characteristics of foreign waters and vessels are to be considered, an absolute analysis of ship traffic distribution characteristics and their integration into the model are necessary. Additionally, it is important to incorporate more detailed operational and environmental characteristics by calculating weights based on navigational situations, such as head-on, overtaking, and crossing situations in each sea area. Lastly, to enhance the reliability of the model presented in this study, it is required to include comparative validation with maritime traffic volume and accident frequency. This aspect is currently being pursued by the author, and more reliable results will be provided in future studies.

Acknowledgments

This research was supported by the "2024 Research Project on the Safety Assessment of Ship Routes" from the Ministry of Oceans and Fisheries.

Fig. 1.
Conceptual Diagram of AIS Data Application
KINPR-2024-48-5-409f1.jpg
Fig. 2.
Overview of SAMR
KINPR-2024-48-5-409f2.jpg
Fig. 3.
MTSI level by spatio-temporal Characteristics
KINPR-2024-48-5-409f3.jpg
Fig. 4.
Visualization based on offshore wind farms and SAMR analysis results
KINPR-2024-48-5-409f4.jpg
Table 1.
Analysis period and range of AIS data
AIS Data Contents
Analysis Period Spring 2020.03.08.-10. (3 Days)
Summer 2020.07.05.-07. (3 Days)
Fall 2020.09.12.-14. (3 Days)
Winter 2020.12.08.-10. (3 Days)
Analysis Range Upper (Latitude) 040°00′N
Left (Longitude) 124°00′E
Lower (Latitude) 032°00′N
Right (Longitude) 132°00′E
Table 2.
Marine traffic characteristics for S1, S2, and S3 per MTSI Level
MTSI Level S1 (m) S2 (Knots) S3 (Times)
1 ~21 ~5.2 ~8
2 22~30 5.3~8.2 9~15
3 31~45 8.3~9.3 16~22
4 46~80 9.4~10.2 23~30
5 81~101 10.3~11.0 31~40
6 102~127 11.1~11.7 41~51
7 128~156 11.8~12.5 52~68
8 157~189 12.6~13.5 69~96
9 190~237 13.6~15.3 97~171
10 238~ 15.4~ 172~
Table 3.
The Status of Weighted Value by 3 Groups
Item wlow wmoderate whigh
Tidal Velocity (Knots) n<1 1n2 2<n
Wave Height (m) n<3 3n5 5<n
Foggy (Days) n<50 50n100 100<n
VTS area Fully Included Partially Included Not Applicable
Table 4.
The analysis results of coastal seas using SAMR
T1 (Cargo Ship) T2 (Tanker)
KINPR-2024-48-5-409i1.jpg KINPR-2024-48-5-409i2.jpg
Table 5.
The analysis results of designated routes using SAMR
Type Ongdo Fairway N.Maemulsudo Fairway S.Maemulsudo Fairway Hongdo Fairway
T1 (Cargo Ship) KINPR-2024-48-5-409i3.jpg KINPR-2024-48-5-409i4.jpg KINPR-2024-48-5-409i5.jpg KINPR-2024-48-5-409i6.jpg
T2 (Tanker) KINPR-2024-48-5-409i7.jpg KINPR-2024-48-5-409i8.jpg KINPR-2024-48-5-409i9.jpg KINPR-2024-48-5-409i10.jpg
Table 6.
Visualization of traffic routes using SAMR
T1 (Cargo Ship)
KINPR-2024-48-5-409i11.jpg KINPR-2024-48-5-409i12.jpg

References

[1] Chae, D. R.(2009), “A study on the necessity of introducing marine spatial planning in Korea”, Journal of the Korean Society of Marine Environment & Safety, Vol. 15, No. 3, pp. 237-242.
[2] Cho, I. S., Lee, J. S. and Kim, H. C.(2023), “Identification of Coastal Maritime Traffic Networks through Spatial Analysis”, Journal of the Korea Institute of Navigation and Port Research, (2023), No. 2, pp. 57-58.
[3] Dawson, J., Pizzolato, L., Howell, S. E. L, Copland, L. and Johnston, M. E.(2018), Temporal and Spatial Patterns of Ship Traffic in the Canadian Arctic from 1990 to 2015, Arctic Press. 711):p. 15-26. JSTOR.
[4] Hwang, H. K., Kim, B. S., Shin, I. S., Song, S. K. and Nam, K. T.(2016), “Development of analysis system for vessel traffic display and statistics based on maritime-bigdata”, Journal of the Korea Institute of Information and Communication Engineering, Vol. 20, No. 6, pp. 1195-1202.
crossref
[5] Kang, W. S. and Park, Y. S.(2022), “A study on the design of coastal fairway width based on a risk assessment model in Korean waterways”, Journal of Applied Sciences, Vol. 12, No. 3, pp. 1535.
crossref
[6] Keum, J. S. and Jang, W. J.(2006), “Evaluation of the navigational risk level in coastal waterway using fuzzy logic”, Journal of the Korean Society of Marine Environment & Safety, Vol. 12, No. 1, pp. 53-59.
[7] Kim, D. H., Kim, J. M., Yoon, B. C., Chang, E. M. and Choi, Y. S.(2015), “Development plan of grid system utilizing spatial information”, Journal of Korea Spatial Information Society, Vol. 23, No. 6, pp. 43-55.
crossref
[8] Kim, H. S.(2024 “A Study on Suitability Assessment Model of Maritime Traffic Routes Based on Spatio-Temporal Operational Environmental Characteri stics”, Korea Maritime and Ocean University, Department of Coast Guards Studies Graduate School, PhD Dissertation..
[9] Kim, H. S., Kang, W. S. and Choi, W. K.(2020), “A Basic Study on the Establishment of Maritime Transportation Network based on Marine Traffic Environment Analysis in Coastal Waters”, Journal of the Korean Society of Marine Environment & Safety, (2020), No. 11, pp. 98.
[10] Kim, J. K.(2021), “Semi-Continuous Spatial Statistical Analysis Using AIS Data for Vessel Traffic Flow Characteristics in Fairway”, Journal of Marine Science and Engineering, Vol. 9, No. 4, pp. 378.
crossref
[11] Kim, T. H., Choi, H. W., Kim, M. G. and Shim, W. J.(2012), “A Spatio-Temporal Variation Pattern of Oiling Status Using Spatial Analysis in Mallipo Beach of Korea”, Journal of the Korean Association of Geographic Information Studies, Vol. 15, No. 4, pp. 90-103.
crossref
[12] Kim, Y. J., Lee, J. S., Pititto, A., Falco, L., Lee, M. S., Yoon, K. K. and Cho, I. S.(2022), “Maritime Traffic Evaluation Using Spatial-Temporal Density Analysis Based on Big AIS Data”, Journal of Applied Sciences, Vol. 12, No. 21, pp. 11246.
crossref
[13] Korea Coast Guard(2024). Concept of Vessel Traffic Service, https://www.kcg.go.kr/kcg/si/sub/info.do?page=2840&mi=2840.
[14] Korea Research Institute for Human Settelments(2011), “Land Use Change Prediction with Spatiotemporal Pattern Analysis and Strategies for Urban Policy”, pp. 3.
[15] Lee, H. T., Lee, J. S., Yang, H. and Cho, I. S.(2021), “An AIS data-driven approach to analyze the pattern of ship trajectories in ports using the DBSCAN algorithm”, Journal of Applied Sciences, Vol. 11, No. 2, pp. 799.
crossref
[16] Lee, M. K., Park, Y. S., Park, S., Lee, E., Park, M. and Kim, N. E.(2021), “Application of collision warning algorithm alarm in fishing vessel’s waterway”, Journal of Applied Sciences, Vol. 11, No. 10, pp. 4479.
crossref
[17] Liye, Z., , Qiang, M. and Tien, F.(2019), “Big AIS data based spatial-temporal analyses of ship traffic in Singapore port waters”, Transportation Research Part E: Logistics and Transportation Review, Vol. 129, pp. 287-304.
crossref
[18] Office of the President. National Tasks(2024). Establishing a World-Leading Maritime Traffic and Logistics System, https://www.president.go.kr/ko/task_new.php.
[19] Oh, J. Y. and Kim, H. J.(2020), “Spatiotemporal Analysis of vessel trajectory data using network analysis”, Journal of the Korean Society of Marine Environment & Safety, Vol. 26, No. 7, pp. 759-766.
crossref
[20] Park, M. J.(2021), “A Basic Study on the Development of the Marine Traffic Risk Index Model”. Korea Maritime and Ocean University, Department of Navigation Science Graduate School; Master’s thesis.
[21] Son, W. J., Lee, J. S., Lee, B. K. and Cho, I. S.(2019), “A Study on the Selection of the Recommended Safety Distance Between Marine Structures and Ships Based on AIS Data”, Journal of the Korea Institute of Navigation and Port Research, Vol. 43, No. 6, pp. 420-428.
[22] Wen, Y., , Huang, Y., Zhou, C., Yang, J., Xiao, C. and Wu, X.(2015), “Modelling of marine traffic flow complexity”, Journal of Ocean Engineering, Vol. 104, pp. 500-510.
crossref
[23] Yoo, Y. and Kim, T. G.(2019), “An Improved Ship Collision Risk Evaluation Method for Korea Maritime Safety Audit Considering Traffic Flow Characteristics”, Journal of Marine Science and Engineering, Vol. 7, pp. 448.
crossref
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