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Compound Flooding in Bangkok and Jakarta: Why Urban Drainage Needs a Multi-Hazard Strategy

In late September 2026, Bangkok and Jakarta offered two different views of the same urban water challenge. Bangkok experienced severe rainfall-driven flooding while authorities were also managing elevated upstream river flows. Meanwhile, Jakarta entered a high-tide warning window along a coast already made more vulnerable by long-term land subsidence. These events were not identical, and the evidence does not show that all flood drivers struck both cities at the same time. However, together they illustrate why compound flooding has become an important design problem for low-lying coastal megacities.

For engineers, developers and city planners, the lesson is therefore more precise than “build bigger drains.” Urban drainage has to work when rainfall, river levels, tides, waves and slow-onset changes such as land subsidence interact or arrive too close together for the system to recover. In practice, that means combining conventional drainage with distributed storage, green stormwater infrastructure and coastal protection rather than relying on one asset to manage every hazard.

Key Takeaways

  • Thailand reported 23 flood-related deaths nationwide and more than 2.5 million people affected between September 16 and the evening of September 28, 2026. Bangkok recorded four of those deaths.
  • All 50 Bangkok districts were declared disaster zones on September 26 after exceptionally heavy rainfall. Bangkok recorded 487 mm from September 1–25, compared with a 1991–2020 September average of 269 mm.
  • Bangkok authorities were simultaneously managing upstream Chao Phraya River inflow. Because river levels were above canal levels, gates had to be closed and water pumped mechanically, showing how pluvial and fluvial conditions can constrain the same drainage network.
  • In Indonesia, BMKG warned on September 29 of 2.5–4 m waves and tidal flooding across ten provinces. Jakarta separately prepared for banjir rob in several northern coastal areas on September 29–30.
  • Importantly, the Jakarta warning should not be presented as proof that four flood drivers occurred simultaneously in the city. Instead, it demonstrates how tidal exposure sits on top of a long-term land-subsidence problem and can combine with rainfall or river flooding when those drivers coincide.
  • A blue-green-grey stormwater management strategy can reduce rainfall runoff at source, add temporary storage when outfalls are constrained and combine nature-based coastal buffers with conventional flood defences.

1. Bangkok Flooding in September 2026: What Actually Happened?

First, Bangkok’s late-September flood emergency was a major rainfall event. By September 26, authorities had expanded the disaster declaration from three eastern districts to all 50 districts. From September 1 to 25, the city recorded 487 mm of rainfall, far above the 269 mm September average for 1991–2020. Moreover, nearly 300 mm fell over roughly 48 hours, creating an estimated 30 million cubic metres of water across the city.

Moreover, the humanitarian impacts extended beyond Bangkok. Thailand’s Department of Disaster Prevention and Mitigation reported that, from September 16 through the evening of September 28, floods had killed 23 people nationwide and affected more than 2.5 million. Four deaths were reported in Bangkok and eight in neighbouring Samut Prakan. At the same time, the Bangkok Metropolitan Administration opened 233 shelters as canals overflowed and thousands of residents moved into temporary accommodation.

However, rainfall alone does not explain the drainage challenge. On September 24, Bangkok officials reported Chao Phraya Dam releases of about 1,700 m³/s. The rate was still below the cited 3,500 m³/s crisis level, yet the river stood above the city’s canal levels. Consequently, drainage gates were closed and water had to be pumped from major canals. Officials also pre-drained canals, used Bueng Nong Bon as retention storage and operated the Phra Khanong pumping station to create additional capacity before further rain.

This is the critical compound flooding lesson from Bangkok. The city was not simply trying to move rainfall through empty pipes. Instead, it was trying to drain a saturated urban catchment while river conditions reduced the ability of the canal network to discharge by gravity. Therefore, even when each individual driver remains below a standalone “crisis” threshold, their interaction can still create serious urban flooding.

2. Jakarta: Tidal Flood Risk on Sinking Ground

In contrast, Jakarta’s situation during the same week was different. Indonesia was experiencing an unusually strong dry-season signal associated with a very strong El Niño. BMKG reported a Southern Oscillation Index of −19.3 and a Niño 3.4 value of +2.53 in its September 25–October 1 outlook. Large parts of Java and other southern regions had also experienced prolonged rainless periods. Nevertheless, coastal water remained a threat.

On September 29, BMKG warned of waves reaching 2.5–4 m in several Indonesian waters and of potential tidal flooding across ten provinces. In Jakarta, the Water Resources Agency separately identified a banjir rob warning window beginning around 18:00 WIB on September 29–30 for areas including Tanjungan, Muara Angke, Muara Baru and Marunda. As a result, pumps, gates, levees, drainage channels and warning systems were expected to be checked before the high-tide period.

Yet accuracy matters here. River flooding in Aceh Tenggara also occurred during the same national weather week, but Aceh is far from Jakarta. Therefore, it should not be combined with the Jakarta tidal warning as if both were one observed local event. Instead, the Indonesian case is useful because it shows how different water hazards can demand attention across one country at the same time, while Jakarta itself remains structurally exposed to future compound flooding when rain, rivers and coastal water overlap.

Land Subsidence Changes the Baseline

Moreover, Jakarta’s long-term vulnerability is intensified by land subsidence. A 2024 BRIN-linked PS-InSAR study measured an average subsidence rate of about 5.71 cm per year across its study data, with stronger subsidence in North and West Jakarta. The study identified excessive groundwater extraction and natural consolidation of alluvial soils as major drivers. Meanwhile, a separate 2026 BRIN assessment reported by The Jakarta Post cited an average of about 3.5 cm per year, with parts of northern Jakarta having sunk by as much as 4 m over four decades.

These figures should not be treated as contradictory measurements of one identical period or method. Rather, they come from different assessments. Nevertheless, both point in the same direction: land subsidence lowers the effective elevation of the city and increases the relative height of tides, coastal water and river stages against urban drainage outlets. Consequently, the same tide can become more damaging as the ground continues to sink.

3. What Is Compound Flooding?

Compound flooding occurs when two or more flood drivers interact in the same place and time window, or in a close enough sequence that their combined impact is greater than considering each driver separately. NOAA identifies precipitation, river discharge, storm surge, waves and tides as key coastal flood drivers. In addition, slow-onset conditions such as land subsidence and sea-level rise can amplify those drivers by changing the baseline on which individual events occur.

In addition, scientific research shows why independence assumptions can be misleading. A 2015 Nature Climate Change study demonstrated that storm surge and heavy precipitation can co-occur and substantially increase flood potential in low-lying coastal cities. Later research in Hydrology and Earth System Sciences examined dependence among oceanographic, fluvial and pluvial drivers and reinforced the importance of considering their relationships rather than modelling every source separately.

For urban drainage design, four layers are especially useful:

  • Pluvial flooding: intense rainfall creates rapid runoff from roofs, roads, plazas and other sealed surfaces.
  • Fluvial flooding: high river discharge raises downstream water levels and can restrict or reverse drainage from canals and outfalls.
  • Tidal and coastal flooding: high tides, waves and storm surge can raise receiving-water levels and reduce the hydraulic head available for drainage.
  • Slow-onset change: land subsidence and sea-level rise gradually make the same urban assets less effective by changing relative elevations.

Importantly, not every flood needs all four layers to qualify as a compound event. Two interacting drivers may be enough. Therefore, the useful planning question is not “Were all four hazards present?” but rather “Which drivers can interact at this site, and what happens when they overlap?”

4. Why Single-Hazard Urban Drainage Can Fail

Traditionally, grey infrastructure is organised asset by asset: pipes manage rainfall, pumping stations move water, levees contain rivers and sea walls resist coastal water. Each can be effective. However, compound flooding exposes the interfaces between them.

For example, a storm sewer may have enough pipe capacity for a design rainfall event. Yet if the receiving river or sea level is unusually high, the outfall loses capacity. Similarly, a pumping station may remove water rapidly, but only while power, mechanical systems and downstream discharge conditions remain available. Meanwhile, a storage basin may fill during the first storm and fail to recover before the next rainfall band arrives.

For example, Bangkok’s September response illustrates this constraint clearly. Because the Chao Phraya was higher than the canals, the city could not rely on gravity drainage in the usual way. Instead, gates were closed and pumping became more important. Thus, the performance of the rainfall drainage system depended on river conditions even though the most visible trigger was heavy rain.

Meanwhile, Jakarta faces a related but slower-moving problem. If ground levels continue to fall relative to the sea, coastal barriers, pumps and outfalls must work against a progressively more difficult hydraulic baseline. Consequently, simply upsizing one pipe or one pump does not solve the entire risk chain.

5. A Blue-Green-Grey Management Train for Compound Flooding

Importantly, no single green roof, detention tank, pump or sea wall can eliminate compound flooding. However, a layered management train can reduce the load at several points in the system. This is where blue-green-grey infrastructure becomes useful.

Step 1: Retain Rainfall at the Roof

Green roofs and rooftop detention reduce the amount and speed of runoff entering street-level drainage during rainfall. In other words, they address the pluvial layer at source. This does not stop tidal flooding, and it does not replace river or coastal defences. Nevertheless, reducing the first surge of runoff can preserve downstream drainage capacity for longer.

Step 2: Slow and Infiltrate Runoff at Ground Level

Bioretention areas, rain gardens, tree pits and permeable surfaces can delay overland flow and, where soil conditions allow, increase infiltration. Moreover, distributed green stormwater infrastructure reduces the dependence on a single downstream pipe. In dense districts, even relatively small source-control areas can become more valuable when they are repeated across many sites.

Step 3: Add Temporary Underground Storage

When gravity outfalls are restricted by high river or tide levels, temporary storage can buy time. Modular underground storage can hold excess stormwater and release it later, after downstream water levels fall. Therefore, storage is not only about total volume; it is also about reset time—how quickly the system can recover before the next rainfall, river or tide peak arrives.

Step 4: Combine Nature-Based Coastal Protection with Grey Defences

At the coast, mangroves can attenuate wave energy and reduce erosion when site conditions are suitable. FAO’s synthesis of field measurements from northern Vietnam reported substantial wave reduction through mature mangrove belts, including measurements of roughly 20% wave-height reduction per 100 m for 5–6-year-old Kandelia candel stands under the reported conditions. However, mangroves are not a universal substitute for engineered coastal protection.

Indonesia’s evolving Giant Sea Wall strategy reflects this hybrid approach. The government’s 2026 master-plan work for the approximately 575 km northern Java programme combines hard coastal infrastructure with mangrove restoration, upstream watershed management and groundwater regulation. Therefore, the strategy increasingly recognises that walls alone cannot address runoff, erosion and land subsidence.

6. How HOENSOEY Components Can Fit Into a Layered System

In practice, product selection should follow the hydraulic function required at each layer. In addition, structural capacity, waterproofing, drainage, overflow routes, saturated weight, planting and maintenance must be coordinated at project level.

HT-508 for Shallow Modular Green Roof Applications

The HOENSOEY HT-508 green roof module uses a 500 × 500 × 80 mm profile. Current product information lists recycled PP construction, four drainage columns and adjustable water-retention components, with approximately 2 L of direct tray water-retention capacity per module. Therefore, it can be considered where a shallow modular green roof profile is appropriate, subject to roof-specific structural and drainage review.

HT-5020 for Deeper Semi-Intensive Green Roofs

The HOENSOEY HT-5020 semi-intensive green roof tray uses a 500 × 500 × 200 mm modular profile with interlocking connections and multi-directional drainage. The current product page lists UV-stabilised high-density polypropylene and about 3.8 L of direct tray water retention per module. Importantly, the 200 mm dimension is the tray profile, not a universal growing-medium depth. Substrate depth and saturated load still need to be verified for each roof.

HOENSOEY Cells for Subsurface Detention

Where a project needs additional temporary underground storage, HOENSOEY Cells provide geocellular components with a published void ratio of approximately 95%. Current component literature also lists vertical compression references above 800 kN/m² and a nominal maximum test reference of 1330 kN/m². However, these are component references rather than automatic project design values. Engineers should verify the applicable test report, material, loading direction, deformation limits, installation build-up and complete system configuration before specification.

In a compound flooding strategy, these components serve different roles. Green roof modules reduce and delay rainfall runoff at source, while underground storage temporarily holds water when downstream drainage is constrained. Neither should be presented as a defence against coastal flooding by itself. Instead, their value comes from reducing the pluvial load on the wider urban drainage system.

7. A Practical Specification Checklist

To design for compound flood risk rather than a single design storm, project teams can use the following sequence:

  1. Map interacting hazards. Model rainfall, river levels, tides, waves and long-term elevation change together where they can influence the same drainage system.
  2. Separate observations from forecasts. Record what has already occurred and clearly label tide, river or rainfall warnings that are still forecasts.
  3. Check outfall constraints. Determine what happens when the river or sea is higher than the site drainage level.
  4. Set source-control targets. Define roof- and site-level retention or detention requirements that reduce peak runoff before it reaches public drainage.
  5. Define a reset-time criterion. Storage should be able to recover between likely successive rainfall, river or tide peaks.
  6. Verify saturated structural loads. Green roof tray height is not the same as substrate depth, and dry weight is not the same as saturated system weight.
  7. Use hybrid coastal protection where appropriate. Combine engineered barriers with mangroves or other nature-based solutions when site conditions and evidence support them.
  8. Address land subsidence. Flood engineering cannot fully compensate for uncontrolled groundwater extraction and continuing ground-level decline.
  9. Plan maintenance from the beginning. Pumps, gates, drains, filters, storage cells and vegetation all lose performance if inspection and maintenance are not funded.

8. What September 2026 Really Tells Us

The September events should not be simplified into a claim that Bangkok and Jakarta both experienced the same four-driver flood at once. The evidence is more useful than that. Bangkok demonstrated how extreme rainfall can overwhelm an urban catchment while river conditions simultaneously limit gravity drainage. Jakarta, meanwhile, demonstrated how a tidal flood warning sits on top of a city already exposed by severe land subsidence.

Together, these cases show why compound flooding is a systems problem. A city may have adequate pipes for rain, a strong levee for the river and pumps for low-lying districts. However, when the receiving water is high, the storage is full or the ground has subsided, the performance of each individual asset changes.

Therefore, resilient urban drainage should be designed as a connected chain: retain water at the roof, slow it across the site, store excess volume, maintain controlled discharge, protect the coast and manage long-term drivers such as groundwater extraction. Ultimately, the goal is not to find one asset that “solves flooding.” It is to create enough distributed capacity and recovery time that the city can continue functioning when multiple hazards overlap.

Frequently Asked Questions

What is compound flooding?

Compound flooding is flooding caused or intensified by two or more interacting drivers, such as heavy rainfall, river discharge, storm surge, waves or high tides. The drivers may occur simultaneously or close enough together that the drainage system cannot recover between them.

Was the September 2026 Bangkok flood a compound flood?

Bangkok clearly experienced severe pluvial flooding while authorities were simultaneously managing elevated Chao Phraya River conditions that restricted gravity drainage from canals. That interaction is consistent with a compound-flooding framework. However, the available evidence does not require claiming that every possible coastal, tidal and subsidence driver was active at the same time.

Did Jakarta experience all four compound-flood drivers in September 2026?

No. The evidence reviewed here supports a tidal-flood warning for Jakarta on September 29–30 and strong long-term vulnerability from land subsidence. River flooding reported in Aceh during the same week occurred in a different region. Therefore, it should not be used as evidence of simultaneous fluvial flooding in Jakarta.

Why is Jakarta particularly vulnerable to tidal flooding?

Jakarta is a low-lying delta city where long-term land subsidence lowers ground levels relative to the sea. Excessive groundwater extraction is a major contributor. As a result, high tides and coastal water can increasingly constrain drainage and affect northern coastal districts.

Can green roofs prevent compound flooding?

No single green roof can prevent compound flooding. However, green roofs can reduce and delay rainfall runoff, which lowers the pluvial load entering urban drainage. When combined with bioretention, temporary storage, pumps, flood barriers and coastal nature-based solutions, they can form one useful layer in a wider stormwater management strategy.

References

  1. Xinhua, “Thailand flood death toll rises to 23,” September 29, 2026.
  2. Europa Press, “All 50 Bangkok districts declared disaster zones,” September 26, 2026.
  3. EFE, “Bangkok in deluge after heavy rains, city on alert,” September 27, 2026.
  4. Prachachat / Bangkok flood-preparation briefing, September 24, 2026.
  5. BMKG, Indonesia weekly weather outlook, September 25–October 1, 2026.
  6. ANTARA, high-wave and tidal-flood warning, September 29, 2026.
  7. Medcom.id, Jakarta tidal-flood preparedness report, September 29, 2026.
  8. Liputan6 / ANTARA, Aceh Tenggara river flooding, September 27, 2026.
  9. Handika, R., Widodo, J. & Pravitasari, A.E. (2024), BRIN-linked Jakarta land-subsidence study.
  10. The Jakarta Post / Asia News Network via China Daily, “Jakarta sinks deeper amid flood risks,” January 29, 2026.
  11. NOAA NCCOS, “Advancing Compound Flood Modeling to Evaluate Coastal Protection Benefits of Natural Infrastructure,” 2025.
  12. Wahl, T. et al. (2015), “Increasing risk of compound flooding from storm surge and rainfall for major US cities,” Nature Climate Change.
  13. Nasr, A.A. et al. (2021), compound flood-driver dependence along the U.S. coastline, Hydrology and Earth System Sciences.
  14. ANTARA, Indonesia Giant Sea Wall master-plan update, September 14, 2026.
  15. FAO, coastal vegetation and wave attenuation synthesis.
  16. HOENSOEY HT-508 product information.
  17. HOENSOEY HT-5020 product information.
  18. HOENSOEY Cells component information.