Category Archive Хроніки війни

ByVladislav Balinsky

201 Vessels Hit — but Not 201 Fires: Satellite Analysis of Operation Molochka

Satellite investigation · Sea of Azov and Black Sea · July 2026

Crimea and the Kerch Strait have become a hub where russia’s military logistics overlap with one of the most vulnerable parts of the Azov–Black Sea basin. The satellite analysis of Operation Molochka examines whether strikes on this system led to mass vessel fires and a new oil catastrophe.

Crimea and the Kerch Strait may be the worst possible location for concentrating fuel logistics anywhere in the Azov–Black Sea region. The narrow, shallow strait connects two marine basins, while the direction of water exchange changes regularly. Pollution entering this area can spread into both the Sea of Azov and the Black Sea, join coastal circulation and reappear hundreds of kilometres from its source.

It is precisely in this environmentally sensitive area that russia concentrated ports, ferry crossings, fuel facilities and a mixed fleet supplying its southern military grouping through occupied Crimea. The July satellite series makes it possible to assess the environmental cost of striking this system.

Satellite analysis of Operation Molochka considers not individual tankers, cargo ships or barges, but the maritime link of a large transport-and-fuel system. Through ports and roadsteads in the Sea of Azov, the Kerch Strait, ferry crossings, warehouses and routes through occupied Crimea, russia sustains military flows on the southern axis.

In the spatial and dynamic analysis of the Kerch logistics hub the Green Leaf team previously showed that transport, fuel and support infrastructure operate here as a single system. Its military function is defined not by a port’s signboard or a vessel’s formal status, but by the flows passing through them. The same principle was formulated in the investigation of the Elektrostal fire: dual use is a property of logistics, not of a single building or vehicle.

For the Kerch hub, this logic carries an especially high environmental cost. Military-significant transport, fuel infrastructure and an ageing fleet are concentrated directly at the hydrodynamic transition between the Sea of Azov and the Black Sea. An accident or rupture of cargo tanks at such a location does not remain local: the substance enters existing natural flows and can be carried far beyond the initial site. The Volgoneft tanker disaster demonstrated this in practice, when heavy fuel oil from the strait was later recorded on the Ukrainian coast.

Environmental vulnerability clearly did not constrain russia when it built this logistics model. On the contrary, civilian ports, merchant vessels, fuel facilities and military flows were brought as close together as possible to make supply routes more resilient. The resulting risk was transferred to both marine basins, their coastal ecosystems and the people living along their shores.

The figure of 201 vessels hit therefore requires an environmental as well as a military reading. The central question is whether an operation of this scale meant dozens of burning tankers, breached cargo tanks and large fields of petroleum products, or whether the strikes mainly removed vessels from the logistics chain without destroying their cargo on a mass scale.

To answer it, the Green Leaf research group and the National Ecological Centre of Ukraine analysed the entire key area: the western Sea of Azov near the Kerch Strait, Temryuk Bay, the Kamennyi Cape area and the roadstead off Primorsko-Akhtarsk. Regional maps show numerous fires on land and around ports, but this investigation focuses on a narrower and more fundamental question: the degree of damage to vessels and the environmental footprint of the maritime part of the operation.

The time series made it possible to isolate two vessel-related episodes and several zones of surface oil pollution. Their relationship to the reported scale of the operation allows the military effect and the environmental cost to be assessed separately.

The assessment used NASA FIRMS thermal detections, Sentinel-2 optical scenes and Sentinel-1 radar imagery from 6 to 27 July. Surface oil pollution was identified using an integrated methodology combining radar detection, optical verification, meteorological correction and analysis of slick movement.

The methodology is described in a scientific paper by Vladyslav Balinskyi, Ruslan Havryliuk, Vitalii Hulevets and Mihaela Timofti: DOI 10.20535/EHS2710-3315.2025.332100. Ambiguous signatures were excluded from the evidence series. Some real slicks may therefore have gone undetected, but the objects presented below are classified as confirmed surface oil pollution.

Limits of the satellite method. Without sampling, it is impossible to determine the specific petroleum product, the thickness of the film or the exact mass released. A satellite image likewise cannot establish the legal responsibility of a particular vessel without AIS records, port data or other independent sources.

Satellite analysis of Operation Molochka: the regional picture

Three NASA FIRMS frames show the same western sector of the Sea of Azov. The one-day scene for 6 July already records a thermal signature at sea. The cumulative view for 6–27 July overlays every thermal event in the interval: many appear on land and near ports, while only one source remains at sea in this sector. The 21 July frame captures the final phase of its thermal activity.

201 reported strikes — and a very different picture at sea: one prolonged thermal source, a second brief smoke episode and several local oil slicks. This ratio is the key to the entire satellite series.

6 July · one day

NASA FIRMS thermal signature in the western Sea of Azov near the Kerch Strait on 6 July 2026, one-day view

6–27 July · three weeks

Three-week NASA FIRMS cumulative view from 6 to 27 July 2026 showing one marine source in the western Sea of Azov

21 July · one day

Final NASA FIRMS thermal detection at the same marine location near the Kerch Strait on 21 July 2026
The same area in the western Sea of Azov. Left: the one-day detection on 6 July. Centre: a cumulative view of all thermal events from 6 to 27 July, showing one marine source amid numerous land and port fires. Right: its final one-day detection on 21 July. NASA FIRMS data. Selection and analysis: Vladyslav Balinskyi.

FIRMS does not prove uninterrupted burning minute by minute, but it records repeated thermal activity at the same location from 6 to 21 July. Within the marine sector examined, this is the only prolonged source of its kind.

The same object was located in Sentinel-2 optical imagery. The 8 and 11 July frames show a vessel and a smoke plume at this point. In the 21 July image the vessel remains in place but is no longer burning or emitting smoke. The final FIRMS detection and the 21 July optical frame are not contradictory: the satellites passed over the area at different times, so FIRMS may have recorded the final phase of the fire several hours before the optical image.

8 July · Sentinel-2

Vessel with a smoke plume in the western Sea of Azov near the Kerch Strait on 8 July 2026

11 July · Sentinel-2

The same vessel with a smoke plume near the Kerch Strait on 11 July 2026

21 July · Sentinel-2

Vessel near the Kerch Strait on 21 July 2026 after the fire ended, with no smoke plume
The Sentinel-2 optical series shows the same vessel in the western Sea of Azov: a smoke plume on 8 and 11 July, and no smoke on 21 July. Copernicus Sentinel data. Analysis: Vladyslav Balinskyi, Green Leaf / NECU.

Confirmed pollution: Temryuk Bay, Kamennyi Cape and Primorsko-Akhtarsk

Radar scenes reveal another part of the picture — not fire, but oil films on the sea surface. In Temryuk Bay they form a separate time series. The pollution itself and its movement are confirmed, but without additional data each slick cannot be attributed to the vessel in the preceding episode.

In Sentinel-1 imagery, the configuration of the slicks changes between 8, 12, 14 and 20 July, while the main plumes shift eastward. In individual frames their measured lengths are approximately 13.07 and 5.37 kilometres.

8 July · Sentinel-1

Confirmed surface oil pollution in Temryuk Bay in a Sentinel-1 image from 8 July 2026

12 July · 13.07 km

Oil slick about 13.07 kilometres long in Temryuk Bay on 12 July 2026

14 July · 5.37 km

Oil slick about 5.37 kilometres long near the eastern part of Temryuk Bay on 14 July 2026

20 July · Sentinel-1

Local surface oil pollution in the eastern part of the observation area on 20 July 2026
Sentinel-1 radar imagery from 8, 12, 14 and 20 July shows changing configurations and the eastward displacement of confirmed surface oil pollution in Temryuk Bay and adjacent sectors. Copernicus Sentinel data. Analysis and measurements: Vladyslav Balinskyi.

Another confirmed episode appears in the 11 July optical frames near Kamennyi Cape. The overview and enlarged image show an elongated area of surface pollution. These frames are important as an independent record, but they should not be tied to a specific vessel or automatically folded into the history of the first source near the Kerch Strait.

Kamennyi Cape · overview

Elongated surface oil pollution near Kamennyi Cape on 11 July 2026, Sentinel-2 optical overview

Kamennyi Cape · enlarged view

Enlarged optical image of elongated surface oil pollution near Kamennyi Cape on 11 July 2026
Confirmed elongated surface oil pollution near Kamennyi Cape on 11 July 2026: overview and enlarged view. Copernicus Sentinel-2 data. Analysis: Vladyslav Balinskyi.

A separate vessel-related episode unfolded much farther east, off Primorsko-Akhtarsk. A Sentinel-2 optical image from 11 July shows a vessel with a substantial smoke plume. This is a different object, unrelated to the prolonged source near the Kerch Strait.

11 July · overview

Separate vessel with a smoke plume on the roadstead off Primorsko-Akhtarsk on 11 July 2026, Sentinel-2 overview

11 July · enlarged view

Enlarged optical image of a vessel with a smoke plume off Primorsko-Akhtarsk on 11 July 2026
The second vessel examined in this article: a smoke plume on the roadstead off Primorsko-Akhtarsk on 11 July 2026. Copernicus Sentinel-2 data. Analysis: Vladyslav Balinskyi.

By 12 July the smoke plume had disappeared, but the environmental episode was not over. A close Sentinel-1 radar frame already shows confirmed surface oil pollution beside the vessel.

Vessel and confirmed surface oil pollution off Primorsko-Akhtarsk in a close Sentinel-1 image from 12 July 2026
Close Sentinel-1 radar image from 12 July: the vessel off Primorsko-Akhtarsk and surface oil pollution extending from it. Copernicus Sentinel data. Analysis: Vladyslav Balinskyi.

The release continues in subsequent scenes. On 14 July one slick measured about 6.64 kilometres. In the final available frame, dated 26 July, a plume about 5.94 kilometres long remained beside the same vessel. Within the analysed series, the pollution therefore persisted from at least 11 to 26 July.

14 July · 6.64 km

Oil slick about 6.64 kilometres long extending from the vessel off Primorsko-Akhtarsk on 14 July 2026

26 July · 5.94 km

Oil slick about 5.94 kilometres long extending from the vessel off Primorsko-Akhtarsk on 26 July 2026
The vessel off Primorsko-Akhtarsk continued to release petroleum products: a slick of about 6.64 km on 14 July and about 5.94 km on 26 July. Copernicus Sentinel data. Analysis and measurements: Vladyslav Balinskyi.

What the ratio of fires and spills reveals about the nature of the operation

When the episodes are viewed at regional scale, the chronology forms a coherent system: a prolonged source near the Kerch Strait, a second vessel off Primorsko-Akhtarsk, and separate pollution events in Temryuk Bay and near Kamennyi Cape. Port and land fires remain a prominent backdrop to the operation, but the maritime component has a different structure.

Both vessels appear to be roughly one hundred metres long. This is consistent with the class of river–sea tankers and product carriers used in the Sea of Azov basin. Reports on the operation named vessels in the same size range, including Sanar-1, Venera-3, Penelope, Chelsea-6 and others. Such ships can therefore be treated as a pool of possible candidates, but the resolution of open imagery does not allow a specific vessel to be identified without AIS, port records or higher-resolution images.

According to the Unmanned Systems Forces, 129 vessels were hit in the Sea of Azov. Against that figure, one prolonged marine source, a second brief smoke event and several local spills are not a minor detail but the central result of the comparison. The mass rupture of cargo tanks on dozens of tankers would have left a fundamentally different signature in the satellite data.

What is visible is consistent with the declared tactic of Ukraine’s Unmanned Systems Forces: depriving vessels of navigation, control and propulsion without turning every strike into a sinking tanker. A satellite cannot see the precise impact point and cannot prove the method used against every vessel. It records the outcome: transport units leave the logistics chain, while the environmental harm, though real, does not grow into a cascading oil catastrophe.

The satellite data do not make this operation “environmentally clean”. They show something different: the harm was localised, while the strike on russian maritime logistics was regional.

The logistical effect of the operation is clearer than an environmental catastrophe. Vessels left roadsteads, reduced their visible activity and concentrated closer to ports and coastal protection. It was this system that carried fuel and military cargo through the Sea of Azov and occupied Crimea.

Two contrasts: Golden Leo and the Volgoneft tankers

The difference between striking military logistics and terror against civilian shipping was expressed most starkly in the Black Sea that same July.

On 19 July, russia attacked the civilian grain carrier Golden Leo with three Kh-59/Kh-69 cruise missiles. One struck the starboard superstructure and a fire broke out aboard the ship. Nine crew members and a Ukrainian pilot were killed; eight people were rescued. The search-and-rescue operation continued throughout the night under the constant threat of further russian strikes. The Ukrainian Navy described the attack as an act of terror against peaceful shipping. A week later, Golden Leo sank. There is no room here for neutral euphemisms: three missiles were launched at an unarmed ship loaded with corn, and ten human lives were taken.

Bulk carrier Golden Leo with a smoke plume after a russian missile strike in the Black Sea on 19 July 2026
Bulk carrier Golden Leo after a russian missile strike in the Black Sea on 19 July 2026. A prolonged smoke plume is visible on the horizon. Photo: Vladyslav Balinskyi.

The history of the Volgoneft tankers provides another contrast. This is no longer a story of local slicks, but of the systemic danger posed by russia’s ageing oil-tanker fleet.

russia’s system for transporting petroleum products through the Sea of Azov and the Kerch Strait was dangerous long before the present war. On 11 November 2007, the tanker Volgoneft-139 broke apart in a storm. More than 1,300 tonnes of heavy fuel oil entered the sea, pollution affected the coast and adjacent waters, and dead and affected birds were counted in the thousands.

In December 2024, the scenario was repeated with Volgoneft-212 and Volgoneft-239. Thousands of tonnes of heavy fuel oil entered the sea, struck the Anapa area and began spreading along the coast. Field and satellite research traced the pollution for at least 600 kilometres to Odesa Region.

These were not random accidents involving isolated ships. Engineer Gennadiy Yegorov warned for years about systemic risks in ageing Volgoneft tankers: corrosion, metal fatigue, inadequate structural margins and dangerous hull conversions. His analysis covered 169 accidents and disasters.

russia’s shadow and auxiliary fleet is therefore dangerous not only as military logistics. The sheer number of ageing tankers, barges and product carriers in a shallow, semi-enclosed sea creates a disaster risk that could exceed the local July releases by hundreds of times.

From satellite observation to evidence

All July episodes are to be added to the Black Sea Environmental Evidence Platform. Each event is assigned a date, coordinates, original imagery, the observation method, an interpretation and clearly stated limits of confidence.

This is especially important for the present investigation. The first vessel-related episode, the pollution in Temryuk Bay, the separate optical episode near Kamennyi Cape and the vessel off Primorsko-Akhtarsk must exist on the map as distinct evidence objects rather than as a single blended narrative.

The Platform does not claim to be a complete register of every pollution event. Conservative selection reduces the risk of false positives, but it also means that some real slicks may have remained outside observation. Every included episode can nevertheless be checked against the original frames and revisited when new AIS records or higher-resolution imagery become available.

Vladyslav Balinskyi certificate for a presentation on tracing oil slicks using Sentinel-1 and Sentinel-2 data
Certificate of Vladyslav Balinskyi’s participation in the 25th International Science Conference “Ecology. Human. Society”, where he presented the integrated methodology for tracing oil slicks using Sentinel-1 and Sentinel-2 data. Kyiv, 12 June 2025.

Satellite analysis of Operation Molochka answers not how many vessels were hit, but what happened to the sea afterwards. The answer cannot be reduced to the word “safe”: one vessel burned for an extended period, another remained a source of petroleum products until at least 26 July, and individual slicks stretched for many kilometres.

At the same time, against the scale of 129 reported strikes, the satellite picture does not resemble the mass breaching of cargo tanks or a series of tanker sinkings. It points to a major logistical effect and a localised environmental footprint. This does not excuse any spill; it records the difference between harm that was constrained and a catastrophe that could have engulfed both marine basins.

That difference is especially stark beside russian practice: the ageing and accident-prone Volgoneft fleet, strikes on Ukrainian ports, and three cruise missiles fired at Golden Leo. In every case the sea becomes a hostage to war. The task of open satellite monitoring is not to strip that emotion from the text, but to support it with evidence that can be checked.

Sources and related material

  1. Suspilne Crimea: Robert Brovdi’s statement on 201 vessels hit.
  2. Reuters Graphics: changes in shipping in the Sea of Azov and the Kerch Strait.
  3. UNN: declared tactic of disabling vessels without breaching cargo tanks.
  4. Ukrainska Pravda: vessels named as hit at the start of the operation.
  5. Reuters: russian strike on the Golden Leo bulk carrier and the deaths of ten people.
  6. Reuters: Golden Leo sank one week after the strike.
  7. The Maritime Executive: the Golden Leo rescue operation under threat of further strikes
  8. UNEP: assessment of the 2007 Volgoneft-139 accident in the Kerch Strait.
  9. Green Leaf: engineering warnings about Volgoneft tankers.
  10. Green Leaf: heavy fuel oil spill and consequences for the Black Sea ecosystem.
  11. Field research in Tuzly Lagoons National Nature Park: heavy fuel oil, war debris and cetacean deaths.
  12. Green Leaf: 900 km² of the Black Sea affected after a russian strike on vegetable-oil tanks.
  13. KPI: Integrated methodology for tracing oil slicks using Sentinel-1 and Sentinel-2 data.
  14. DOI for the scientific paper on the integrated methodology.
  15. Environmental Evidence Platform: interactive map of pollution and damage in the Black Sea.
  16. Full scientific and methodological description of the Environmental Evidence Platform.

Monitoring and preparation of evidentiary material are carried out through cooperation between the Green Leaf NGO, the National Ecological Centre of Ukraine and Tuzly Lagoons National Nature Park, with support from Deutsche Bundesstiftung Umwelt (DBU). The scientific content, interpretations and conclusions are the responsibility of the authors and participating organisations and do not necessarily reflect the position of DBU.

ByГерасимова Тетяна

Scientific Research into War Impacts on the Black Sea Coast in Tuzly Lagoons National Nature Park

Language version: Read this article in Ukrainian.

The international SUNDANSE project team is studying war impacts on the Black Sea coast in Tuzly Lagoons National Nature Park.

The expedition combined ecological monitoring with documentation of the effects of Russia’s military aggression on marine ecosystems.

Three specialists took part in the field research:

  • Vladyslav Balinsky — head of the Odesa branch of the National Ecological Centre of Ukraine and a research scientist at Tuzly Lagoons National Nature Park;
  • Ruslan Havryliuk — head of the National Ecological Centre of Ukraine and deputy director of the Institute of Geological Sciences of the National Academy of Sciences of Ukraine;
  • Ivan Rusev — head of the Research Department of Tuzly Lagoons National Nature Park.
Aerial view of the sandy barrier in Tuzly Lagoons National Nature Park between the lagoons and the Black Sea
The sandy barrier separating the Tuzly Lagoons system from the Black Sea. Photo: Vladyslav Balinsky

War impacts on the Black Sea coast

The sandy barrier separates the Tuzly Lagoons system from the Black Sea. It is the largest remaining natural section of Ukraine’s marine coast. Today, the area is increasingly affected by the war.

During the expedition, researchers found fragments of Russian aerial vehicles. They also recorded new deaths of Black Sea cetaceans and discovered heavy fuel oil on the shore. The pollutant continues to wash ashore after the December 2024 tanker accident near the Kerch Strait.

During the survey, the team documented:

  • debris from Russian aerial vehicles on the sandy barrier;
  • fresh heavy fuel oil clumps and older fragments partly covered by sand;
  • new deaths of Black Sea cetaceans.
Fragment of a Russian aerial vehicle found on the coast of Tuzly Lagoons National Nature Park
A fragment of an aerial vehicle found during the coastal survey in Tuzly Lagoons National Nature Park. Photo: Vladyslav Balinsky
Missile or aerial vehicle debris on the sandy Black Sea coast in Tuzly Lagoons National Nature Park
Another fragment found on the sandy barrier during field monitoring. Photo: Ruslan Havryliuk

Heavy fuel oil pollution persists after the tanker accident

One of the expedition’s main tasks was to search for new signs of heavy fuel oil pollution. Ruslan Havryliuk conducts this research within the international OIL-TRACE Black Sea project.

Its full title is Remote and Field Monitoring of Oil Pollution Dynamics in the Kerch Strait and the Tuzly Lagoons Region. The project is implemented with support from the German Federal Environmental Foundation (Deutsche Bundesstiftung Umwelt, DBU).

The field survey showed that the sea is still bringing new heavy fuel oil fragments ashore more than a year and a half after the accident.

Researchers found fresh clumps lying directly on the sand. Older fragments were already partly covered by sand deposits. This indicates that the pollutant continues to move with marine currents and periodically returns to the coast.

Ruslan Havryliuk holding a heavy fuel oil fragment found on the coast of Tuzly Lagoons National Nature Park
Heavy fuel oil fragment washed onto the sandy Black Sea coast

Heavy fuel oil fragments washed onto the coast of Tuzly Lagoons National Nature Park after the Russian tanker accident. Photo: Vladyslav Balinsky

How heavy fuel oil moves through the marine environment

According to Ruslan Havryliuk, satellite monitoring and field verification made it possible to trace the movement of the pollution. After the accident, heavy fuel oil migrated at least 600 kilometres along Ukraine’s Black Sea coast.

Much of the pollutant is not on the water surface. It can remain in the water column and bottom sediments. During strong storms, it may re-enter the water and contaminate the marine environment again.

The consequences are therefore not short-lived. They may persist for many years.

The spread of pollution into valuable protected areas of the north-western Black Sea is a particular concern. These areas include Tuzly Lagoons National Nature Park, adjacent protected waters and the Danube Biosphere Reserve.

Heavy fuel oil contaminates sediments and harms coastal ecosystems. It disrupts beach microbial communities and creates additional risks for birds and other marine wildlife.

Field research also verifies satellite observations directly on the ground. Combining the two methods helps researchers trace the pollution and build a scientific evidence base for documenting environmental damage caused by Russia’s aggression.

The number of dead Black Sea cetaceans continues to rise

The expedition also continued monitoring marine mammal deaths. The new findings indicate that the situation is deteriorating further.

According to Ivan Rusev, head of the Park’s Research Department, 12 more dead Black Sea harbour porpoises (Phocoena phocoena relicta) were found in the park between 3 and 8 July.

Dead bottlenose dolphin on the coast of Tuzly Lagoons National Nature Park
A dead bottlenose dolphin on the coast of Tuzly Lagoons National Nature Park. Photo: Vladyslav Balinsky

From late May to early July 2026, 74 dead Black Sea cetaceans were officially recorded in the park.

The Black Sea harbour porpoise is listed as Endangered (EN) on the IUCN Red List.

Researchers stress that official figures show only a small part of the real losses. They estimate that about 95% of dead cetaceans never reach the shore.

Bodies that wash ashore may be carried back to sea by waves. Jackals can also drag them into dense coastal vegetation before scientists or border guards document the findings.

Expert estimates cited in the field report suggest that tens of thousands of Black Sea cetaceans may have died during the first half of 2026. Total losses since the start of Russia’s full-scale invasion may exceed 100,000 animals.

Field data for international research projects

The survey was coordinated with the international SUNDANSE project. One of its tasks is to study the long-term environmental consequences of the destruction of the Kakhovka Hydroelectric Power Plant for the Black Sea.

The project systematises data on sediments released from the former Kakhovka Reservoir. Researchers study their composition, movement and effects on marine ecosystems.

They also analyse coastal pollution, changes in benthic ecosystems and the accumulation of hazardous substances in the marine environment.

Field surveys help assess war impacts on the Black Sea coast in a comprehensive way. Records of heavy fuel oil pollution, cetacean deaths and other wartime damage complement satellite monitoring. Together, these data support an evidence base on the environmental consequences of Russia’s aggression against Ukraine.

Data from the expedition are used in both SUNDANSE and OIL-TRACE Black Sea. This connects sediment transport research with documentation of long-term oil pollution and its effects on marine ecosystems.

Author: Tetiana Herasymova

An earlier version of this material was also published by the National Ecological Centre of Ukraine.

Deutsche Bundesstiftung Umwelt, German Federal Environmental Foundation

The monitoring was carried out with support from the Deutsche Bundesstiftung Umwelt (DBU, German Federal Environmental Foundation) under its programme supporting Ukrainian researchers and environmental professionals. The publication’s content, interpretation of data and conclusions are the responsibility of the authors and do not necessarily reflect the position of DBU.

ByVladislav Balinsky

Environmental Evidence Platform: Interactive Map of Pollution and Damage to the Black Sea

The interactive Black Sea pollution map combines satellite data, field observations, laboratory material and verified sources. It supports the documentation of environmental damage caused by russia’s aggression against Ukraine.

How to use the map. Open the layer catalogue, select an event or evidence type, and click a point, line or polygon. The object card provides the date, coordinates, observation method, photographs, sources and scientific cautions. Open the map full screen.

This platform was not created for neutral observation of the war. The russian federation is the aggressor state, and its full-scale invasion has caused extensive and long-term damage to Ukraine’s environment, including the marine and coastal ecosystems of the Black Sea.

The United Nations General Assembly formally defined russia’s actions as aggression against Ukraine. The UN Environment Programme also documents the war’s broad environmental consequences and their regional implications for the Black Sea.

Official Ukrainian assessments already measure damage to the Black Sea and Sea of Azov in the hundreds of billions of hryvnias. The real loss, however, is not limited to clean-up costs or damaged property. It includes habitat degradation, animal mortality and displacement, loss of ecosystem functions, persistent contamination, broken scientific time series and reduced capacity for recovery.

When an incident exists only as a news item, social-media post, photograph or satellite image, it can remain in the information space without becoming verifiable evidence. Investigation requires a date, coordinates, the original file, a named author or source, the acquisition method, links to related material and an honest statement of uncertainty.

This is why NGO Green Leaf, scientists from Tuzly Lagoons National Nature Park and project lead Ruslan Havryliuk developed a tool that brings these materials together in a single geospatial environment.

Each point, line or polygon opens not merely a symbol but an evidence card containing the date, coordinates, observation method, photographs, satellite material, sources, scientific interpretation and remaining uncertainty.

The platform is designed to preserve, verify and organise material that may be important for investigations of environmental crimes, possible war crimes, proceedings concerning ecocide under Ukrainian law, and future claims for compensation and reparations. The map does not issue legal judgments: legal qualification belongs to investigators, prosecutors, experts and courts. Our task is to prevent evidence from disappearing, preserve its provenance and make the verification method transparent.

The platform is not a complete register of every pollution event in the Black Sea. It includes incidents for which the team has sufficiently reliable satellite, field, laboratory or documentary material. The absence of an event from the map must not be interpreted as evidence that no pollution occurred.

Why the marine environment requires a dedicated evidence system

During war, the sea is one of the least accessible environments for regular scientific monitoring. The occupation of Crimea, hostilities, mine danger, attacks on ports and vessels, navigation restrictions and risks to research teams make the conventional model of systematic ship-based observation impossible across substantial parts of the marine area. Actual access changes with the security situation and cannot honestly be reduced to one stable percentage.

Under these conditions, open satellite data, field verification along accessible coastlines, laboratory analysis and secure preservation of media become core rather than supplementary tools. They make it possible to observe processes where a research vessel cannot safely operate, while also showing where remote interpretation requires field or laboratory confirmation.

Evidence for damage assessment and compensation

Documentation is directly connected to future compensation. Category B3.1 of the Register of Damage Caused by the Aggression of the russian federation Against Ukraine expressly covers environmental damage, monitoring and assessment costs, restoration measures and loss of intrinsic ecological value.

Evidence collected and organised today can therefore form an initial layer for future state claims for compensation and reparations. Formal submission will still require separate authentication and action by the competent authorities.

International scientific cooperation

The platform is also an appeal to the international scientific community. Ukrainian researchers need more than statements of solidarity: they need access to satellite archives and computing capacity, laboratory facilities, equipment, secure repositories, international expertise and support for safe field missions. Without such support, a substantial share of marine damage will remain undocumented.

From initial cases to a scalable system

The current edition grew out of the documentation of three events with different physical and ecological characteristics: the Volgoneft-212 and Volgoneft-239 tanker disaster and heavy-fuel-oil pollution; the vegetable-oil spill associated with the Port of Pivdennyi (VO-1); and the spill associated with the Port of Chornomorsk (VO-2).

These cases do not define the final boundaries of the project. They form the first fully developed test of a common approach that can be applied to new accidents, damaged vessels, consequences of Russian strikes on port and maritime infrastructure, affected habitats, animal mortality and other forms of environmental harm.

Every event uses the same internal logic:

  • source and primary release;
  • development and transport;
  • field evidence and sampling;
  • biological and habitat impacts;
  • analytical reconstruction.

This structure reveals a complete causal chain rather than an isolated dark patch on a satellite image. It connects a probable source with immediate and delayed effects, including secondary accumulation of contaminants in bottom sediments and their later remobilisation into the water column and marine circulation.

This is especially important in the semi-enclosed Black Sea: the disappearance of a surface slick does not mean that the impact has ended. Basin-scale cyclonic circulation generally proceeds counterclockwise and can transport tracers between eastern and northwestern sectors, including towards the Odesa coast and the Danube Delta.

The actual pathway of each event nevertheless depends on wind, waves, mesoscale eddies, stratification and local currents. It must therefore be assessed event by event using satellite, field and modelling evidence: Black Sea circulation, variable Kerch Strait exchange, and post-depositional remobilisation.

The map is also a georeferenced media repository. Users can move from a mapped object to a photograph, a satellite crop, an analytical document or a public source. This is useful for scientists, protected-area staff, journalists, civil-society organisations, investigators and experts who need to understand not only what is shown, but what evidence supports the description.

How an evidence object is built

The principal unit of the platform is not the layer or the symbol, but the evidence object. It may be a field-observation point, the boundary of a satellite anomaly, an affected habitat, a sampling site, the position of a vessel fragment or a reconstructed transport line. Each card contains complete English and Ukrainian sections so that the material can support both national and international communication.

How to read the map geometry:

  • Points mark observations, finds, sampling locations or probable sources.
  • Lines show documented movement or cautiously framed analytical reconstructions.
  • Polygons outline interpreted boundaries of satellite anomalies, contaminated areas or affected habitats.

The cards distinguish three levels. Direct observation is what is recorded in an image, in the field or in a document. Interpretation is the scientific explanation of that observation. Analytical reconstruction is the reconstruction of a probable source, pathway or relationship between separate observations. Keeping these levels separate reduces the risk that a working hypothesis will be read as a directly established fact.

Data provenance is preserved in the same way: photographer, institution providing field material, person responsible for samples, laboratory or media partner, and source of satellite data. A numerical laboratory value is not assigned to an individual point unless the sample identifier, location and date can be matched explicitly.

Satellite methodology and field verification

Radar and optical satellite data

The remote-sensing workflow integrates radar data from Sentinel-1 and optical imagery from Sentinel-2. Radar makes it possible to examine the sea surface independently of daylight and with substantial all-weather capability.

Surface films can damp short waves and produce dark anomalies in SAR imagery. Similar signatures may also be caused by low wind, natural surfactants, atmospheric processes or current boundaries. A dark area is therefore an analytical lead rather than automatic proof of pollution.

Sentinel-2 helps verify boundaries, colour and structure, and can reveal dense accumulations, emulsions and individual surface objects. Time-series analysis is combined with meteorological conditions, slick morphology and independent evidence. Where an underwater leak is suspected, backward tracing relates persistent dark-core zones to the direction of transport, water depth and the estimated rise of particles from the source to the surface.

The approach is described in the published paper Integrated methodology for tracing oil slicks using Sentinel-1 and Sentinel-2 data: backward modelling, meteorological correction, and visualization analysis, presented in the proceedings of the “Ecology. Human. Society” conference; DOI: 10.20535/EHS2710-3315.2025.332100.

Field verification

Satellite interpretation does not replace fieldwork. In Tuzly Lagoons National Nature Park, field verification is conducted by the Park’s Research Department under the scientific supervision of Ivan Rusev. It includes GPS positioning, photography, descriptions of substrates and habitat condition, biological observations and sample collection. Ruslan Havryliuk coordinates sample records, integration of laboratory data and scientific interpretation of analytical results.

Three current cases — the first operational edition

Volgoneft. This module combines accident and wreck locations, dated satellite observations, probable residual leak sources, drift reconstructions and M-series field points documenting heavy-fuel-oil contamination. A central task is to show where direct evidence ends and where the hypothesis of long-range transport toward the Odesa coast begins.

VO-1. The vegetable-oil spill associated with the Port of Pivdennyi demonstrates the temporal development of an industrial surface film and the way its visibility changes between radar and optical imagery.

VO-2. The event associated with the Port of Chornomorsk provides the most complete chain, from the port source and satellite dynamics to field and biological verification. It includes FP-1, FP-2 and FP-3, documented by Ivan Rusev and the Park’s Research Department: impact on a protected sandy barrier, a psammophilic habitat and vegetable-oil film or emulsion in coastal waters.

Together, these modules show that the same architecture can be used for different pollutants and evidence types. Future events will be added as new modules within the existing system rather than through the creation of a separate map from the beginning.

Media repository, data provenance and limits of inference

Photographs, satellite crops and documents are not treated as decorative illustrations. They remain linked to a specific place and statement. Media are attached to an existing evidence object when they describe the same spatial situation. A separate media point is created only when the material has independent spatial meaning.

M-series heavy-fuel-oil field photographs and materials are attributed to Vladyslav Balinsky and Ivan Rusev according to the current register. FP-1, FP-2 and FP-3 materials were provided by Ivan Rusev and Tuzly Lagoons National Nature Park. Analytical data associated with the M-6/M-7 survey were obtained within the work of the International Charitable Organization Environment–People–Law and provided to the project by Olena Kravchenko.

The platform is designed to preserve material that may be important for investigations of environmental crimes, possible war crimes, proceedings concerning ecocide, and claims for compensation and reparations. Publication on the map does not replace procedural authentication, a proper chain of custody, laboratory traceability, independent expert validation or a decision by a competent authority.

Who develops and maintains the platform

Vladyslav Balinsky — remote-sensing methodology; Sentinel-1 and Sentinel-2 processing and interpretation; scientific mapping; field verification; evidence-system architecture; and publication preparation; Research Department, Tuzly Lagoons National Nature Park.

Ruslan Havryliuk — project leadership; scientific coordination; sample and laboratory-data coordination; integration of analytical results; and scientific review.

Ivan Rusev — scientific supervision of field verification; biological and ecosystem interpretation; validation and provision of field materials from Tuzly Lagoons National Nature Park.

NGO Green Leaf is the project’s publication and media platform. Related institutional and project materials are published by the National Ecological Centre of Ukraine, including the SUNDANSE project page.

The platform is developed and implemented with support from the German Federal Environmental Foundation — Deutsche Bundesstiftung Umwelt (DBU), project 30025/100. The authors and partner organisations gratefully acknowledge DBU grant support. Scientific content, interpretations and conclusions remain the responsibility of the authors and participating organisations.

This work also has a personal dimension. In January 2026, the National Ecological Centre of Ukraine reported systematic persecution, in-absentia criminal proceedings and direct threats against Vladyslav Balinskyy connected with his role in documenting war crimes and acts of ecocide.

This is another reason why an evidence base must not depend on the safety of one person or remain in a private archive. It should be distributed, open to verification and institutionally protected.

How to use the map and what comes next

Open the layer catalogue, select an event and click an object. Its evidence card provides photographs, sources, documents, the observation method and limitations. Satellite and field polygons are scientific interpretations of spatial evidence rather than perfectly exact physical boundaries of pollution.

Submit material. Photographs and reports of heavy fuel oil, petroleum, vegetable oil, dead or affected dolphins, birds and other biota can be sent to zeleniy.list1@gmail.com. Please include the original photographs, date, location or coordinates and a short description. Do not place yourself at risk in order to document an event.

The public map is a viewing and verification interface. It does not replace protected storage of original files, the internal evidence register or a procedural chain of custody.

  • For social media, press communication and general sharing, use the URL of this article.
  • For full-screen analysis, use the direct uMap link.
  • For scientific use, open the individual evidence card and review its sources and limitations.
  • The platform will be expanded as new verified data and event modules become available.

Read the full scientific and methodological description

Language version: Читати українською.


Suggested citation: Balinsky, V.; Havryliuk, R.; Rusev, I. Environmental Evidence Platform: Interactive Map of Pollution and Damage to the Black Sea. NGO Green Leaf, 2026. The map is a living resource; an access date should be included when citing it.

An adapted institutional version of this publication is also available from the National Ecological Centre of Ukraine: “How Ukraine Is Documenting Environmental Damage to the Black Sea” .

Deutsche Bundesstiftung Umwelt — German Federal Environmental Foundation

The monitoring was carried out with the support of Deutsche Bundesstiftung Umwelt (DBU, German Federal Environmental Foundation) under its programme supporting Ukrainian researchers and conservation professionals. The content of this publication, the interpretation of the data and the conclusions are the responsibility of the authors and do not necessarily reflect the position of DBU.

ByVladislav Balinsky

Elektrostal, July 2026: A Spatial-Dynamic Analysis of the Environmental Consequences of Strikes on Logistics and Fuel Infrastructure

Sentinel-2 imagery, atmospheric transport, combustion chemistry, public-health risks, and the limits of official air-quality monitoring

Vladislav Balinsky — chemist, biologist, and editor-in-chief of the online environmental outlet Zelenyi Lyst

Why This Analysis Matters

We are not examining this incident because the fire itself is inherently compelling.

During the night of 18 July 2026, drones struck two facilities in the Moscow region: the Wildberries logistics centre in Elektrostal and an oil depot in Noginsk. According to RT, 24 people were injured in Elektrostal; one of them later died in hospital.

When we examined Sentinel-2 imagery acquired on 19 July, we saw that the smoke did not disperse over empty countryside. It moved across a densely populated area and, in the near-source zone, remained close to the ground. This raises the obvious environmental-health questions: what was in that air, and what were local residents told?

Key finding. The satellite image matters here not as a photograph of a fire, but as a snapshot of the spatial structure of atmospheric transport of combustion products.

The official response came quickly. On 18 July, the same day as the strikes, RIA Novosti, citing the Moscow Region Ministry of Ecology and Natural Resources, reported that no exceedances of ambient-air quality standards had been identified in Elektrostal or the Bogorodsky district. Rossiyskaya Gazeta relayed the same wording, but added a detail that should not be overlooked: no exceedances had been recorded, yet a smell of burning was reported at several locations.

A smell of burning is not a metaphor. It is the human sensory detection of combustion products in air. In other words, substances were present at concentrations high enough to be smelled, while the instruments reportedly registered nothing of concern. How is that possible? The answer lies in what was actually measured.

RT, also citing the ministry, stated that 20 fixed monitoring stations sample between five and eight parameters. Kommersant added that a mobile laboratory operated by Mosoblekomonitoring was working at the site and could measure 32 parameters.

Now consider what was burning: approximately 250,000 square metres of marketplace goods, including PVC packaging, synthetic textiles, polyurethane, consumer electronics, and lithium-ion batteries. Such a fire may generate hydrogen cyanide, phosgene, hydrogen chloride, hydrogen fluoride, dioxins, furans, and polycyclic aromatic hydrocarbons.

Standard urban air-monitoring stations do not normally measure most of these compounds. They measure the pollutants for which they were designed: carbon monoxide, nitrogen and sulphur oxides, and particulate matter. Dioxins cannot be detected by rapid field methods at all; they require chromatographic mass-spectrometric analysis and laboratory processing that may take weeks.

One qualification is essential. The ministry did not specify which five to eight parameters were measured, so our assessment is based on the general operating practice of such stations. If cyanides, phosgene, and organochlorine compounds were in fact analysed, that can be demonstrated easily: publish the measurement protocols. The question could be settled within a day.

What “No Exceedances Were Recorded” Actually Means

The ministry’s statement concerns air — more precisely, the samples collected by instruments on 18 July. That information is useful. But a fire of this type raises four distinct questions, and the statement addresses only one of them.

Air while the fire is burning. Concentrations are highest during active combustion, and this is when monitoring matters most. Yet an instrument can report only what it is designed to detect. If cyanides, phosgene, and organochlorine compounds are not on the analytical list, they will not appear in the report — even if they are present. In this context, “no exceedances” means only “no exceedances among the substances that were tested.”

Air after the flames have been knocked down. Monitoring reportedly continued until the fires were fully contained, which is logical from a narrow air-quality perspective: once combustion stops, the emission source diminishes. But containment does not mean the event is over. Debris removal and water application continued for several days, while oxygen-deficient smouldering can generate substantial concentrations of incomplete-combustion products. People working or living nearby may therefore remain exposed after routine measurements have ceased.

People. This is no longer an air-sampling question. Phosgene may produce delayed effects: a person can inhale it during the fire, feel relatively well the next day, and develop pulmonary oedema 24 to 48 hours later. By that point, measuring the air may be meaningless — the air may be cleaner while the person is not. Medical observation for at least 72 hours is required in suspected exposure scenarios. No public reports indicated that such monitoring had been organised in Elektrostal or Noginsk.

Soil and what grows on it. Dioxins are not captured by rapid field methods. They deposit onto soil and water and can subsequently enter vegetables, milk, and fish. Detecting them requires laboratory analysis of environmental samples after the fire has been extinguished, followed by monitoring over months. No such programme was publicly reported.

Of the four questions, the official response therefore addresses only one — and even that only partially.

Debris That Falls by Itself

Now consider not the figures, but the language. In this case, words perform almost as much work as instruments.

The governor of the Moscow region stated that a fire broke out when one of the drones fell. Grammatically, the drone did not strike; it fell. The fire was not caused by an impact; it simply occurred. The sentence contains no acting subject, no strike, and not even a clearly identified object that was hit. There is only a naturalised sequence: something fell, and something caught fire.

This is not an isolated communications failure. It is a stable construction familiar from Russian official reporting in recent years: not “a strike on an oil depot,” but “falling UAV debris”; not “an impact,” but “a fire caused by falling debris.” In this linguistic world, the debris exists independently. It is no longer part of something that was flying towards and struck a target.

The air-quality statement is built on the same principle. Note the wording: not “the air is clean” or “there is no danger,” but “no exceedances of standards were recorded.” Formally, this is not a statement about the condition of the air. It is a statement about the act of recording. It is difficult to refute because it makes no direct claim about the environment; it says only that the instruments did not register an exceedance.

And in the same communication, several locations were reported to have a smell of burning.

This is where the language reveals its function. “Smell” is an everyday word: scorched food, a neighbour’s bonfire. It does not belong to the vocabulary of hazard. Yet a smell of burning is precisely the sensory detection of airborne pollutants by people in places where the instruments supposedly recorded nothing.

Three elements form a single communications structure. There is no actor who struck the target — only debris that fell. There is no pollution — only exceedances that were not recorded. There are no toxicants — only a smell of burning.

This formula can be named in different ways, but its function is clear: to reduce public alarm without making a directly falsifiable statement. Each individual phrase is defensible. The danger lies in their combination.

There is another important circumstance. This is not a remote province where information takes weeks to circulate. It is the Moscow region: densely populated, adjacent to the capital, equipped with an extensive monitoring network, and covered by dozens of newsrooms. There is no shortage of instruments, journalists, or opportunities to ask questions. The wording is therefore less plausibly explained by a lack of data than by a deliberate choice.

The speed of reassurance is also revealing. The calming conclusion was published on 18 July — the same day as the incident and before the fire had been contained.

A Comparison: Tuapse, Three Months Earlier

To understand how far this response departs from an established pattern, consider a case we analysed in the spring.

After strikes on the Tuapse oil terminal on 16 and 20 April 2026, Rospotrebnadzor recorded concentrations of benzene, xylene, and soot at two to three times the maximum permissible levels. The Krasnodar regional emergency headquarters advised residents to remain indoors unless necessary and to keep windows closed.

The same state apparatus, the same country, three months apart. In Elektrostal, where a far more heterogeneous and potentially more toxic mixture was burning than crude oil alone, the public message was that nothing had been detected.

There are two possible explanations. Either the air in Elektrostal was genuinely cleaner than in Tuapse, which is physically difficult to reconcile with the nature of the fuel load, or the difference lay in what was measured and what authorities chose to disclose.

It is important to stress that all the reporting cited above comes from RIA Novosti, Rossiyskaya Gazeta, RT, Kommersant, and official statements by the relevant Russian ministry. No Ukrainian source is required for this comparison. We have simply placed those reports alongside one another and compared them with what is visible in the satellite imagery.

We begin with that imagery.

1. What the Satellite Revealed

The Sentinel-2 image was acquired on 19 July, approximately 30 hours after the strike. It therefore does not show the peak burning phase, but a later stage characterised by residual combustion, smouldering, and intensive water application.

Two distinct source areas are clearly visible: a compact, dense plume near Elektrostal and a broader, more diffuse smoke veil over Noginsk, extending eastward along the M-7 motorway. Importantly, we identified this two-source structure in the image before cross-checking it against media reporting. The reports subsequently confirmed two affected facilities: the Wildberries logistics centre, covering approximately 250,000 square metres, and an oil-depot fire in Noginsk.

The light-grey colour of the plume is consistent with a late fire phase in which smouldering and heavy water application predominate. This does not imply that the incident was minor. At the time of acquisition, the source areas remained active; the main fire was reportedly contained only during the second half of 19 July.

For this analysis, the image is not merely a photograph of a fire. It is a snapshot of the spatial structure of atmospheric transport of combustion products.

Супутниковий знімок Sentinel-2 пожежі в Електросталі та Ногінську, 20 липня 2026 року

Figure 1. Sentinel-2 image acquired approximately 30 hours after the strike. Two smoke sources are visible: the logistics complex in Elektrostal and the oil depot in Noginsk.

2. More Than Oil Was Burning — and That Complicates the Forecast

The two fire sources involved fundamentally different combustion chemistry. This is not a secondary detail; it is the foundation of the risk assessment.

An oil-depot fire produces a comparatively predictable emissions profile: carbon and sulphur oxides, soot, polycyclic aromatic hydrocarbons, and volatile organic compounds. We examined this profile in detail in our earlier analysis of Russian oil refineries.

A 250,000-square-metre logistics complex is a different type of source. Its potential fuel load includes plastics, PVC packaging, synthetic textiles, polyurethane, cardboard, consumer electronics, and lithium-ion batteries. Where substantial quantities of PVC undergo thermal decomposition, chlorine-containing combustion products are expected, creating conditions under which dioxins and furans may form. Lithium-ion batteries may contribute hydrogen fluoride and metal oxides; synthetic materials may generate cyanide compounds.

In other words, this incident activates a specific rule in our model: chlorine-containing materials can sharply alter the hazard profile and require long-term environmental response, not merely fire suppression.

3. Four Different Risks, Not One

The practical implication of this chemical profile is that there is no single hazard. There are at least four, separated in time and requiring different response protocols.

The first minutes. Synthetic materials and polyurethane can release hydrogen cyanide during combustion. It inhibits cellular respiration and can act within minutes. Carbon monoxide, acrolein, hydrogen chloride from PVC, and hydrogen fluoride from batteries may add to the acute hazard. At this stage, the decisive factor is the speed of evacuation; medical intervention may come too late for those with severe exposure.

One to three days. This is the most deceptive interval. In cooler combustion zones, phosgene may form under appropriate conditions in the presence of chlorine-containing compounds. Toxic pulmonary oedema can then develop after a delay, when the exposed person is already at home and feels relatively well. Hospitalisation during the first night is therefore not a guarantee of safety; observation should continue for at least 72 hours.

Several days for those working at the site. Debris removal and prolonged water application entail repeated work in a smouldering zone, where concentrations of incomplete-combustion products may remain high. Ordinary filtering respirators are not sufficient against carbon monoxide, hydrogen cyanide, or phosgene. Positive-pressure self-contained breathing apparatus is required.

Years. Dioxins, furans, and metals released from electronics create a different risk horizon involving soil, food chains, and long-term medical surveillance. This is the fourth layer of response — and the one for which no public programme was reported.

4. Who Is Affected — and Who Will Not Appear in the Reports

We can now apply this temporal framework to what is known about the people involved.

Official reports referred to 24 injured people in Elektrostal and two in Noginsk. One of the injured later died in hospital, meaning that even the initial casualty figures changed.

These figures represent acute trauma: burns, blast fragments, and poisoning during the first hours. By definition, they do not capture three other groups.

People beneath the plume. When populated areas are exposed to combustion products, increases in presentations for hypertensive crises, arrhythmias, asthma attacks, and exacerbations of chronic obstructive pulmonary disease are statistically expected, especially among older people and those with chronic illness. This is not a claim about specific undocumented cases; it is a well-established pattern in smoke-affected populations. The absence of public data does not prove that no effect occurred. It may simply mean that no one counted it.

Emergency responders. This is probably the most heavily exposed group and one of the least discussed. Many effects may be delayed, which is precisely why responders require structured medical observation rather than ceremonial praise in a press release.

People whose clinical window had not yet closed. At the time of publication, approximately three days had passed since the night of 18 July — exactly the interval in which delayed pulmonary oedema may become apparent. People who initially felt well and did not seek help could therefore have been entering the most critical phase. This was not a future forecast; it was the risk window open at the time the article was published.

5. Where the Plume Went

The remaining question is geographical: how far were the combustion products transported?

In the near-source zone, the plume moved towards the north-east and then turned northward. Its geometry does not show an abrupt shift in direction or pronounced fragmentation, suggesting relatively stable air-mass transport during a substantial part of the fire.

Супутниковий знімок Sentinel-2 району Електросталі та Ногінська із просторово протяжним шлейфом продуктів горіння.

Figure 2. Sentinel-2, 19 July 2026. The visible smoke-plume axis extends northward from Elektrostal and Noginsk, passing east of Sergiyev Posad. Source: Sentinel-2, European Space Agency.

The optically dense portion of the plume can be followed with confidence for approximately 300 kilometres: through the Orekhovo-Zuyevo area, east of Sergiyev Posad, and towards the Rybinsk Reservoir. This trajectory crosses parts of the Moscow and Yaroslavl regions and may have affected the western edge of the Vladimir region.

The 300-kilometre estimate applies only to the part of the plume visible in the imagery. Fine particles and gaseous combustion products may have travelled farther; beyond a certain distance, they are simply no longer distinguishable in the optical image.

One further observation is important for understanding the transport mechanism. Near the source, the smoke remained low and close to the surface. Farther away, it became elevated and diffuse within the atmospheric boundary layer. This is a typical transition from near-source ground-level pollution to regional transport, and it helps explain why different zones require different response protocols.

During this particular meteorological window, the principal atmospheric burden remained over Russian territory. No transport towards Ukraine was observed. Under different meteorological conditions, the spatial pattern would have been different.

6. A Brief Note on the Legal Framework

Because this analysis concerns the consequences of a strike, the status of the targeted facility cannot be ignored.

A logistics hub of this scale may serve both civilian and military supply chains. Dual use is not necessarily a property of a building itself; it is a property of the logistical flows passing through it. Ukrainian sources have stated that such hubs were used to supply sanctioned components for drones and navigation equipment. Russian military bloggers also publicly asked where drones and fibre-optic cable would now be procured.

There is currently no direct open-source confirmation of the contents of this particular warehouse, and that limitation must be acknowledged. At the same time, Articles 57 and 58 of Additional Protocol I to the Geneva Conventions require parties controlling territory to take precautions and, to the extent feasible, separate military objectives from civilian populations and civilian objects. Where military logistics are routed through civilian infrastructure, risks to civilians arise in large part from that organisational choice.

7. Conclusions

This case is not maritime. It involves a different mode of transport, different chemical profiles, and a different legal framework. Yet the model operates in the same way.

Atmospheric transport determined the spatial structure of risk. Combustion chemistry determined its temporal dynamics. The configuration of the logistics hub informed the legal character of the object.

Our spatial-dynamic model makes it possible to:

identify primary impact zones;

separate risks by time scale — minutes, days, weeks, and years;

determine who requires immediate evacuation, who needs 72-hour medical observation, and where soil monitoring may be the appropriate response;

assess the legal character of an object through the function of logistical flows rather than the nominal status of a building.

This brings us back to the starting point.

Strikes on oil depots and logistics centres have more than an economic dimension. They also have environmental and public-health consequences for people living nearby. That principle applies regardless of the side involved or the territory affected.

Residents of Noginsk and Elektrostal were not told what symptoms might emerge a day later. They were not told who should seek medical attention. Responders were not publicly warned that a filtering respirator is not adequate protection in a smouldering zone.

At this point, the conclusion must be stated plainly. The problem was not an absence of capacity. The Moscow region operates 20 fixed stations and a mobile laboratory covering 32 parameters. Three months earlier in Tuapse, the same state system publicly reported concentrations two to three times above permissible limits and advised residents to keep their windows closed. The instruments exist. The specialists exist. The experience exists.

The selection of analytical parameters therefore cannot be dismissed simply as ignorance. Compiling a panel that excludes the compounds most relevant to this particular fire requires an understanding of which compounds are relevant. It is competence applied in the opposite direction.

This leads to a broader conclusion.

What is concealed is usually something whose consequences are understood. Silence of this quality is rarely the product of mere negligence; it is the product of work. That implies that actors within the system understand both the scale of what occurred and the circumstances in which it began — not with debris falling in isolation, but with the war launched and continued by the Russian state, for whose environmental consequences it will bear responsibility alongside the rest.

That responsibility does not disappear because it was not documented domestically.

One final point concerns Ukraine.

Ukraine remains under continual attack. Part of its territory is occupied. Its own ecosystems are being destroyed: the destruction of the Kakhovka Dam, pollution of the Black Sea, and millions of hectares of mined, burned, and degraded land. Yet Ukrainian civil-society organisations continue to document the environmental consequences of the war not only in Ukraine, but also within the territory of the aggressor state.

This is not because Ukraine lacks other priorities. It is because the environmental consequences of this war will eventually have to be assessed in full — on both sides of the front line, using a consistent methodology and without exceptions. We have an interest in making that accounting accurate. Those who remain silent about fires on their own territory do not share that interest in precision — and that, too, is evidence.

Postscript

This article continues Zelenyi Lyst’s series on the environmental consequences of strikes on infrastructure. Earlier case studies examined Tuapse in April 2026 and the Kerch Strait in June 2026. The model remains unchanged from case to case; only the specific transport parameters, chemical profiles, and legal frameworks vary. In our view, that consistency is what distinguishes a working analytical model from a collection of unrelated incident descriptions.

Sources

Event and air-monitoring data: RIA Novosti, Rossiyskaya Gazeta, RT, and Kommersant, 18 July 2026, citing the Moscow Region Ministry of Ecology and Natural Resources. Satellite data: Sentinel-2, European Space Agency, 19 July 2026.