The Construction of Seaports in the Arctic: Prospects and Environmental Consequences
Abstract
:1. Introduction
- Marine technologies for the safe use, operation and protection of the Arctic marine ecosystem;
- Marine food systems represented by value chains in fisheries, aquaculture and seafood trade;
- Marine biotechnology and bio-products;
- Application of scientific and engineering principles to the processing of materials by marine biological agents for the provision of goods and services;
- Maritime transport via the NSR, which increases the stability of navigation through the use of modern Russian icebreakers.
- Analysis of the development of Russian seaports in the Arctic;
- Identification of anthropogenic threats and ways to ensure environmental safety for the Arctic seas;
- Ontological engineering of the subject area for the purpose of developing an RMS.
2. Literature Review on Port Infrastructure Development: Logistics, Ecology, Risks
2.1. Logistics, Process Management
2.2. Tourism
2.3. Power Consumption in Ports
2.4. Port Emissions, Environmental Risks
3. Analysis of Research on Smart Ports, New Technologies and Development Prospects
3.1. Port Sustainability and Efficiency through New Technologies
3.2. Smart Port Management
3.3. Energy Efficiency SP
3.4. Self-Driving Vehicles in SP
3.5. Safety in SP
4. Materials and Methods
- Waste water: Vessels occasionally release waste water, sewage and bilge water, which typically contains oil contamination. These discharges are controlled by national, regional and local agencies, encompassing harbor authorities as well.
- Vessel paint: The release of hazardous paint substances intended to hinder shell adherence to ships may damage aquatic organisms.
- Storm drains: Rainwater drains gather contaminants from the port’s hard surfaces and release them into the water, frequently circumventing treatment centers.
- Nitrogen: As the primary contributor to eutrophication in oceanic environments, nitrogen results in proliferating algae that deplete the water’s oxygen, leading to the demise of fish and shellfish populations.
- Oil spills: Pollution from oil can encompass persistent contamination due to runoff, discharge from bilge, oil tanker transfers and substantial spills that occur from tanker overflow or breaches in ship hulls.
- Dredging: The process of eliminating sediment to expand navigational routes may heighten water cloudiness, disturb contaminated sediments, harm or demolish crucial habitats for wildlife and disturb or annihilate vulnerable and threatened species.
- Foreign species: Marine creatures may hitch a ride on ships through ballast water, utilized for stabilizing vessels, and subsequently be introduced to foreign environments, posing a risk as invasive species that disrupt the equilibrium of native ecosystems.
- Human health.
- Ecosystem status.
- (1)
- Conceptualization, implying the identification of concepts and relationships between them in the interrelated areas of risk management, the subject area and the field of data mining, as well as the generation of accurate and clear textual definitions of concepts and relationships;
- (2)
- Formalization, in which a formal model of the concepts and relationships identified at the previous stage is created;
- (3)
- Implementation in the language of ontology representation.
- (4)
- Clarification and harmonization of terminology of different fields and port activities;
- (5)
- Definitions of basic concepts in the study of the anthropogenic effects of port on the natural environment;
- (6)
- Systematization of interrelations between concepts and identification of classes and subclasses of ontologies;
- (7)
- Structuring of knowledge and information, taking into account the research being carried out.
5. Results and Discussion
5.1. Classification of Ports as Sources of Risk
- (a)
- geographical location;
- (b)
- Attitude to international trade;
- (c)
- Volume of annual cargo turnover;
- (d)
- Appointment;
- (e)
- Annual duration of operation;
- (f)
- Relation to water level.
- Those located in deep natural bays protected from the open sea by capes acting as natural breakwaters (for example, Yokohama, New York, Rio de Janeiro, Istanbul);
- Those located in shallow bays or on coastal plains, where protection from the open sea is provided by artificial breakwaters (for example, Casablanca);
- Those located in estuaries of navigable rivers away from the mouth (for example, Hamburg, Le Havre, London, Montevideo, Montreal).
5.2. Ports of the Russian Arctic Zone: Current Status and Development Prospects
5.3. Risks in the Expansion of Shipping in the Arctic: Negative Consequences of Port Activities
- (1)
- By their nature—mechanical, physical or chemical;
- (2)
- By their physical properties—substance, process, phenomenon and object;
- (3)
- According to the stability of changes they cause in nature—temporary reversible changes, relatively irreversible changes, absolutely irreversible changes and anthropogenic stress on ecosystems;
- (4)
- Based on the ability to accumulate—either at the time of production or over an extended period;
- (5)
- Determined by the frequency—as either a continuous, periodic or sporadic factor;
- (6)
- According to the ability to migrate—non-migrating, migrating with the flow of air or water, migrating with means of production or migrating independently.
- Risk reduction by lowering the level of threat implementation conditions (vulnerabilities) through the use of protection mechanisms;
- Risk prevention by avoiding the threat or eliminating the source of the threat;
- Acceptance of negative consequences and absence of any actions to reduce the level of risk or to transfer risk, i.e., full or partial transfer of responsibility for the consequences of the realization of an adverse event to third parties (insurance).
6. Conclusions
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Conflicts of Interest
References
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Region | Port | The Area of the Seaport Territory (ha) | The Area of the Seaport Water Area (km2) | Number of Berths/Piers | Length of the Berthing Front of the Seaport (p.m) | Maximum Dimensions of Vessels Entering the Port (m) | The Period of Navigation in the Seaport | ||
---|---|---|---|---|---|---|---|---|---|
Precipitation | Length | Width | |||||||
Ports of the Western Arctic | Murmansk | 645.9 | 53.7 | 111/2 | 13246.48 | Not limited | year-round | ||
Arkhangelsk | 215.26 | 1120 | 75/0 | 8884.14 | 9.2 | 190 | 30 | year-round | |
Kandalaksha | 25.44 | 5.09 | 5/0 | 584.45 | 9.8 | 200 | 33 | year-round | |
Vitino | 18.66 | 11.59 | 4/0 | 512 | 11.1 | 230 | 32.2 | year-round | |
Onega | 2.68 | 845.59 | 7/0 | 880 | 13.6 | 242 | 32.4 | year-round | |
Mezen | 191 | 191 | 3/0 | 215 | 4.2 | 120 | 20 | 01.05–01.10 | |
Varandei | 1.47 | 24.98 | 2/0 | 199.86 | 3.5 | 120 | 15 | 01.06–30.12 | |
Naryan-Mar | 22.5697 | 5.6256 | 6/0 | 730.66 | Mixed-navigation vessels (river–sea)/sea vessels | June–November | |||
3.6/3.6 | 114/90 | 14/16 | |||||||
Sabetta | 179.5 | 1177 | 11/0 | 2 365.8 | 12 | 315 | 50 | year-round | |
Dudinka | 24.92 | 30.22 | 9/0 | 1 723.6 | 11.8 | 260.3 | 32.2 | 01.01–20.05, 15.06–31.12 | |
Dixon | 4.77 | 0.182 | 2/0 | 243 | 8.0 | 100 | 20 | June–October | |
Khatanga | 10.62 | 3.70 | 5/0 | 400 | 4.17 | 136 | 16.5 | June–October | |
Ports of the Eastern Arctic | Tiksi | 7.29 | 96.78 | 2/0 | 315.0 | 3.9 | 129.5 | 15.8 | 15.07–30.09 |
Pevek | 19 | 8.9 | 3/0 | 500 | 9 | 172.2 | 24.55 | 03.07–25.10 | |
Anadyr | 11.89 | 45.33 | 6/0 | 686 | 7 | 177 | 25 | 01.07–01.10 | |
Provideniya | 12.7 | 13.02 | 4/0 | 350.82 | 10 | 200 | 24 | 01.06–01.12 | |
Egvekinot | 7.17 | 5.75 | 2/0 | 570.62 | 7.5 | 150 | 21 | July–November | |
Beringovsky | 22.12 | 47.07 | 4/0 | 269 | 13 | 190 | 33 | 01.07–01.10 |
Risk | Environmental Risk | Information Safety Risk |
---|---|---|
Potential threat | Natural (man-made, anthropogenic) danger | Threat |
Conditions for the implementation of the threat | Vulnerability of the environment | Vulnerability |
Adverse event | Negative impact on the environment | Attack |
Consequences of the occurrence of the event | Adverse changes in the natural environment | Damage |
Valuable resources | Natural environment | Information assets |
Resource quality | Environmental quality | Quality of information |
Required resource properties | Necessary environmental properties | Information safety properties |
Protection mechanisms | Environmental protection measures | Information protection mechanisms |
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Makarova, I.; Buyvol, P.; Mukhametdinov, E.; Boyko, A. The Construction of Seaports in the Arctic: Prospects and Environmental Consequences. J. Mar. Sci. Eng. 2023, 11, 1902. https://doi.org/10.3390/jmse11101902
Makarova I, Buyvol P, Mukhametdinov E, Boyko A. The Construction of Seaports in the Arctic: Prospects and Environmental Consequences. Journal of Marine Science and Engineering. 2023; 11(10):1902. https://doi.org/10.3390/jmse11101902
Chicago/Turabian StyleMakarova, Irina, Polina Buyvol, Eduard Mukhametdinov, and Aleksey Boyko. 2023. "The Construction of Seaports in the Arctic: Prospects and Environmental Consequences" Journal of Marine Science and Engineering 11, no. 10: 1902. https://doi.org/10.3390/jmse11101902
APA StyleMakarova, I., Buyvol, P., Mukhametdinov, E., & Boyko, A. (2023). The Construction of Seaports in the Arctic: Prospects and Environmental Consequences. Journal of Marine Science and Engineering, 11(10), 1902. https://doi.org/10.3390/jmse11101902