Problems of the management of habitat monitoring in settlements (ports) of the Northern Sea Route

Introduction. The Northern Sea Route (NSR) is the main Arctic shipping route in the Russian Federation. As part of the development of Arctic infrastructure, the state and private investors have launched large-scale work on the development of Arctic ports.

The purpose of the study was to evaluate the current monitoring system for the state of atmospheric air, soil, and drinking water in the territory of settlements (ports) in the Northern Sea Route.

Materials and methods. Official data from environmental pollution monitoring by (Russian Federal Service for Hydrometeorology and Environmental Monitoring (Roshydromet) and social and hygienic monitoring by Federal Service for Supervision in Protection of the Rights of Consumer and Man Wellbeing (Rospotrebnadzor) in twelve settlements and ports in the Northern Sea Route were used. An electronic database has been created. The analysis was carried out using MS Office Excel, visualization of the location of monitoring points – ESRI ArcGIS 9.3

Results. The conducted research has shown heterogeneity in the management of monitoring of environmental factors of the population living in settlements (ports) of the NSR. The largest monitoring coverage is typical for settlements in the North-West – primarily the cities of Murmansk and Arkhangelsk, where the largest number of posts are located and all environments are monitored – atmospheric air, soil of populated areas and drinking water. There is practically no monitoring of the habitat in the village of Sabetta, Dudinka. In the village. Dixon habitat monitoring is not carried out. Atmospheric air, the quality of which is especially important for territories with developed port infrastructure, is controlled only in 5 out of 12 settlements (ports) of the NSR.

Limitations. The research had no limitations.

Conclusion. The need to optimize the monitoring system was noted. As measures, it is recommended to manage monitoring of atmospheric air, drinking water, and soil in the village. Dixon; atmospheric air and soil in the village. Sabetta and Dudinka; atmospheric air in Beringovsky village, Igarka, Providence village; soil in Tiksi village. It is necessary to expand the list of controlled indices in atmospheric air, drinking water and soil, as well as increase the frequency of sampling.

Compliance with ethical standards. The study does not require the submission of a biomedical ethics committee opinion or other documents.

Contribution:
Myasnikov I.O.– concept and design of the study, collection and processing of material, responsibility for the integrity and proportionality of all parts of the article;
Kizeev A.N.– literature analysis, data analysis, editing of the text of the article;
Fedorov V.N. – statistical analysis, interpretation of results, editing of the text of the article;
Tikhonova N.A. – analysis data, editing the text of the article;
Novikova Yu.A. – data analysis, correction of the research design, editing the text of the article.
All co-authors – approval of the final version of the article.

Conflict of interest. The authors declare no conflict of interest.

Acknowledgement. The study had no sponsorship.

Received: May 3, 2024 / Accepted: June 19, 2024 / Published: September 10, 2024