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Lewisham Air Quality Monitoring – Proposals for Change

Executive Summary

Lewisham’s air quality monitoring network currently consists of five continuous reference monitors and 162 diffusion tubes changed monthly by a contractor. While diffusion tubes provide broad spatial coverage, they are costly (£19,409 per year including contractor fees) and limited to monthly averages, restricting their ability to capture short‑term pollution episodes, diurnal patterns, or acute exposure risks. Sensors cannot be used to assess compliance with statutory limits but they play an increasingly important role in public information, engagement, and local exposure assessment.

Lewisham already operates 6 Praxis Cube multi‑pollutant sensors, and a further 11 MCERTS‑certified multi-pollutant sensors will be added in 2026 through existing funding. These additions significantly enhance the borough’s real‑time monitoring capability and provide a strong foundation for expanding non‑statutory monitoring to support public health messaging and community engagement.

The recent Coroner’s concerns emphasise the need for more granular, real‑time public information to help residents reduce exposure during high‑pollution periods. Diffusion tubes alone cannot meet this expectation. Modern sensor technologies—MCERTS‑certified particulate monitors, low‑cost outdoor sensors (AirGradient), indoor monitors (AirGradient Indoor, Airthings View Plus), and mobile personal exposure devices (Atmotube PRO)—offer flexible, scalable options that complement statutory monitoring and strengthen public access to timely information.

Reducing diffusion tube numbers by 50–75% would release £9,704–£14,556 annually, enabling substantial reinvestment in real‑time sensors without increasing overall budget. This creates a strong financial case for rebalancing the network while retaining statutory compliance through reference monitors.

A mixed monitoring strategy offers the best balance of accuracy, cost efficiency, and public value. A small number of MCERTS sensors should be deployed at strategic locations to anchor the network and validate low‑cost devices. Borough‑wide coverage could be expanded using AirGradient outdoor sensors, which provide high‑resolution real‑time data at very low cost. Indoor sensors could be deployed selectively in schools and vulnerable settings, while Atmotube mobile sensors or similar can support engagement, personal exposure studies, and hotspot investigation.

This approach directly addresses the Coroner’s concerns by improving public access to timely, detailed air quality information, enabling residents to make informed decisions during pollution episodes. It also reduces recurring costs, increases flexibility, and strengthens Lewisham’s ability to target interventions, support schools, and engage communities.

Recommendation:
Lewisham should adopt a phased transition toward a sensor‑led monitoring network, reducing diffusion tube numbers and reinvesting savings into a mixed portfolio of MCERTS, low‑cost outdoor, indoor, and mobile sensors. This strategy enhances public information, supports community engagement, complements statutory monitoring, and provides the most cost‑effective and future‑proof approach for the borough.

Introduction

The purpose of this document is to review Lewisham’s current air quality monitoring arrangements and consider whether they remain fit for purpose. In doing so, it asks three core questions:

1. What do we want to learn from the data?
Is the primary aim to track compliance with statutory objectives, to understand local exposure hotspots, or to evaluate the impact of specific interventions? Each purpose requires a different level of spatial and temporal resolution, and not all monitoring technologies are equally suited to every question.

2. Do we need new equipment to answer these questions?
In many cases, existing reference‑grade monitors—supported by modelled background maps, diffusion tube networks, or targeted short‑term studies—may already provide sufficient evidence. Before expanding the network, it is important to establish whether the desired insight genuinely requires additional instrumentation or whether improvements in analysis, validation, or integration would achieve the same outcome.

3. What are the available options?
Low‑cost sensors can increase spatial coverage and support community engagement, but they introduce greater uncertainty and require careful calibration and interpretation. Reference‑grade monitors and a diffusion tube network remain essential for statutory compliance and long‑term trend analysis. Diffusion tubes offer excellent spatial coverage at low cost, but they are limited to monthly averages and cannot capture short‑term peaks, diurnal patterns, or episodic events that may significantly influence annual mean exposure. In some cases, mobile monitoring, short‑term deployments, or enhanced modelling may provide more actionable insight than permanent installations.

Ultimately, changes to the monitoring network should be driven by clear evidence of gaps in spatial coverage, suspected localised sources contributing disproportionately to exposure, or a need for more granular temporal information. In many situations, strengthening data quality, validation processes, and integration with public health evidence may deliver greater value than simply adding more monitors.

A potential future direction is the development of a citizen‑science programme. Such initiatives can broaden monitoring coverage, reveal hidden vulnerabilities, and give communities a stronger voice in shaping fairer policies. However, challenges remain around data quality, integration with formal reporting frameworks, and ensuring inclusive participation without inadvertently excluding or stigmatizing vulnerable groups.

Current Situation

Five continuous monitoring stations were operational within the London Borough of Lewisham (LBL) during 2025. The former LW1 Catford site—now designated LW6—was relocated in November 2021 to Laurence House, 1 Catford Road, where it continues to measure nitrogen dioxide (NO₂). The Deptford site (LW5), also measuring NO₂, was decommissioned in April 2025. A Defra funded project enabled the instillation of six Praxis Cubes during 2025 and during 2026 a further 11 sensors will be installed, likely to be Airlys. The Council also undertake non-automatic (diffusion tube) monitoring of NO2 at 148 locations.

The following charts illustrate current monitoring coverage in Lewisham and also the concentrations of Nitrogen dioxide that they measure. This information can be used too determine the usefulness of the data that is being collected and where are the gaps.

Core Data

  • Diffusion tubes (2019–2025) +
  • LAEI 2022 traffic data major roads
  • AQMA boundaries
Diffusion Tube Counts by NO₂ Concentration Band
year 20–25 µg/m³ 25–30 µg/m³ >30 µg/m³ NA 15–20 µg/m³ <15 µg/m³
2019 12 18 20 98 0 0
2020 40 22 5 49 32 0
2021 38 17 6 47 39 1
2022 41 20 7 8 68 4
2023 38 12 6 4 74 14
2024 28 13 3 2 68 34
2025 34 12 2 0 76 24

Diffusion tube locations and concentrations (1999 - 2025), with major roads and AQMA boundaries.

Locations with concentrations above 25µg/m3 within 5km of a road.

Locations with concentrations below 15µg/m3 within 5km of a road.

What next?

Coroner’s Concerns

In the Prevention of Future Deaths (‘PFD’) report for the inquest of Ella Adoo Kissi-Debrah, the Coroner identified several issues that pose a continuing risk unless further action is taken. One of the key concerns relevant to Lewisham’s monitoring strategy was the low level of public awareness about air pollution information sources, such as the UK‑Air website and local pollution alerts. The Coroner noted that improving public access to timely, detailed air quality information could help individuals reduce their personal exposure, particularly during high‑pollution episodes.

The Coroner also highlighted that providing sufficiently granular and locally relevant information is likely to require expanded monitoring capacity, including an increased number of air quality sensors. This expectation applies to both national and local government.

This creates a clear strategic question for Lewisham: how can the borough strengthen public access to reliable, real‑time air quality information while maintaining a monitoring network that is proportionate, cost‑effective, and aligned with statutory requirements?

Proposals for Change

Proposal 1 — Maintain the current monitoring approach, but expand the sensor network using external funding

This option preserves the existing balance of reference monitors, sensors and diffusion tubes while adding an additional modest number of low‑cost or MCERTS‑indicative certified sensors. It is operationally simple and low‑risk. However, diffusion tubes remain the dominant source of spatial data, meaning monthly averages continue to limit temporal insight. Public access to real‑time information improves, but only incrementally.

Proposal 2 — Gradually shift towards a sensor‑led network, reducing reliance on diffusion tubes

This option shifts Lewisham toward a more modern, sensor‑led monitoring network. Reducing diffusion tube numbers frees up recurring budget that can be reinvested in low‑cost sensors, MCERTS‑certified particulate monitors, or personal/indoor monitoring devices. This approach directly addresses the Coroner’s concerns by increasing the availability of detailed, real‑time information and enabling more targeted public health messaging.

It does, however, require careful planning around calibration, QA/QC, and integration with existing reporting frameworks.

Tube Reduction Annual Saving
25% (40 tubes) £1,836
50% (80 tubes) £3,672
75% (120 tubes) £5,508

A key consideration under this proposal is what types of sensors to purchase and how they will be deployed. Options include:

  • Ambient outdoor sensors (multi‑pollutant, low‑cost) to increase spatial coverage
  • Personal exposure sensors to support targeted studies or community engagement
  • Indoor air quality sensors for schools, workplaces, or vulnerable households
    This approach aligns with the Coroner’s concerns by improving public access to detailed, timely information, but it requires careful planning around data quality, calibration, and integration with existing reporting frameworks.

Decision‑Making Matrix: Options for Evolving Lewisham’s Air Quality Monitoring Network This matrix compares the two proposals currently under consideration, incorporating known costs, operational implications, and alignment with the Coroner’s concerns regarding public access to detailed, real‑time air quality information.

Costed Scenario Analysis: Expansion of Lewisham’s Sensor Network

This analysis models the financial implications of expanding Lewisham’s air quality sensor network under three deployment scenarios: 10 sensors, 20 sensors, and 50 sensors.
Costs are based on currently available pricing for Breathe London (Airly) MCERTS‑certified sensors, with optional comparison to AirGradient Open Air (non‑MCERTS, low‑cost, used by Reading and other Local Authorities for engagement).

Diffusion tube costs are included to show potential savings if Lewisham reduces tube numbers under Proposal 2.

1. Baseline Costs

Diffusion Tubes (Current)

  • 160 tubes
  • £3.75 per tube per month
  • 12 months
  • Annual cost: £7,344
    • Tubes: £7,200
    • Carriage: £144

If Lewisham reduces tube numbers, savings scale linearly:

Tube Reduction Annual Saving
25% (40 tubes) £1,836
50% (80 tubes) £3,672
75% (120 tubes) £5,508

These savings can be reinvested into sensors under Proposal 2.

2. Sensor Cost Assumptions

Breathe London / Airly (MCERTS PM)

  • 3‑year contract (non‑solar): £4,085 per sensor
  • 5‑year contract (non‑solar): £6,075 per sensor
  • Annual MCERTS removal/reinstallation: £350 per sensor

AirGradient Open Air

  • Assembled: USD225 (~£175)
  • Kit: USD125 (~£95)
  • No MCERTS
  • Suitable for engagement, schools, citizen science

3. Scenario Costs (MCERTS Sensors)

Scenario A — 10 Sensors

3‑Year Contract - Sensor cost: 10 × £4,085 = £40,850 - Calibration every 2 years 10 × £350 = £3,500 - Total 3‑year cost: £44,350

5‑Year Contract - Sensor cost: 10 × £6,075 = £60,750 - Calibration every 2 years: 10 × £350 × 2 = £7,000 - Total 5‑year cost: £67,750

Scenario B — 20 Sensors

3‑Year Contract - Sensor cost: 20 × £4,085 = £81,700 - Calibration every 2 years: 20 × £350 = £7,000 - Total 3‑year cost: £88,700

5‑Year Contract - Sensor cost: 20 × £6,075 = £121,500 - Calibration every 2 years: 20 × £350 × 2 = £14,000 - Total 5‑year cost: £135,500

Scenario C — 50 Sensors

3‑Year Contract - Sensor cost: 50 × £4,085 = £204,250 - Calibration every 2 years: 50 × £350 = £17,500 - Total 3‑year cost: £221,750

5‑Year Contract - Sensor cost: 50 × £6,075 = £303,750 - Calibration every 2 years: 50 × £350 × 2 = £35,500 - Total 5‑year cost: £339,250

4. AirGradient Scenario Costs (Non‑MCERTS)

These are dramatically cheaper and suitable for:

  • schools
  • indoor monitoring
  • citizen science
  • engagement
  • hotspot investigation

10 Sensors

  • 10 × £175 = £1,750

20 Sensors

  • 20 × £175 = £3,500

50 Sensors

  • 50 × £175 = £8,750

These basic sensors do not require data management like the Praxis Cube or Airly. However it would be prudent for a member of staff to sense check the data on a regular basis and collocating the sensor with a reference monitor for 2 weeks once a year would only enhance the data collected.

5. Combined Strategy Options

Option A — MCERTS + AirGradient Mix

For example:

  • 10 MCERTS sensors (compliance + public alerts)
  • 20 AirGradient sensors (schools + engagement)

Cost (3‑year): - MCERTS: £44,350
- AirGradient: £3,500
- Total: £47,850

Option B — Reduce Diffusion Tubes by 50%

Savings: £3,672 per year

This could fund: - 21 AirGradient sensors per year, or
- 1 MCERTS sensor every 1.1 years

6. Management Interpretation

10 Sensors

  • Modest expansion
  • Good for hotspot validation and public alerts
  • Low operational burden

20 Sensors

  • Borough‑wide coverage
  • Supports school engagement, public dashboards, and targeted interventions
  • Strong alignment with Coroner’s concerns

50 Sensors

  • High‑resolution network
  • Enables street‑level mapping and real‑time public exposure reduction
  • Significant cost; requires robust QA/QC and data management

Total Cost Comparison Chart (10, 20, 50 sensors)

Annualised Cost Comparison Chart

Cost per Sensor Type (Unit Cost Chart) ## *Air Quality Monitoring – Risk Register**

This risk register compares the two strategic proposals:

  • Proposal 1: Maintain current monitoring network + expand sensors using MAQF funding
  • Proposal 2: Expand sensors + reduce diffusion tubes + reinvest savings

It also includes risks associated with specific technologies (MCERTS, AirGradient, Airthings, Atmotube).

1. Strategic Risks

Risk Description Likelihood Impact Mitigation
Misalignment with Coroner’s concerns If monitoring remains heavily reliant on diffusion tubes, Lewisham may not meet expectations for more granular, real‑time public information. Medium High Expand sensor network; improve public dashboards; reduce tube reliance over time.
Insufficient spatial coverage Maintaining current network may fail to identify localised hotspots or exposure risks. Medium Medium Deploy low‑cost sensors in schools, residential areas, and suspected hotspots.
Over‑expansion without QA/QC Rapid sensor deployment without calibration or validation could reduce data reliability. Medium High Develop QA/QC protocol; pair low‑cost sensors with MCERTS reference points.
Technology obsolescence Sensors may become outdated or unsupported within 3–5 years. Medium Medium Choose open‑source or widely adopted platforms; plan for replacement cycles.

2. Financial Risks

Risk Description Likelihood Impact Mitigation
High recurring cost of diffusion tubes Current annual cost (£19,409 including contractor) limits ability to invest in sensors. High High Reduce tube numbers; reinvest savings into sensors.
High capital cost of MCERTS sensors MCERTS sensors cost £4,085–£6,075 each + £350 annual maintenance. High High Deploy only at strategic locations; supplement with low‑cost sensors.
Underestimating installation/maintenance costs MCERTS sensors require annual removal/reinstallation (~£350). Medium Medium Include full lifecycle costs in budgeting.
Exchange rate volatility (USD → GBP) AirGradient indoor/outdoor pricing may fluctuate. Medium Low Use conservative conversion rates; include contingency.

3. Operational Risks

Risk Description Likelihood Impact Mitigation
Data integration challenges Multiple sensor types may produce inconsistent formats or require new workflows. Medium Medium Standardise data ingestion; use platforms compatible with multiple devices.
Maintenance burden Large sensor networks require regular checks, calibration, and replacement. Medium Medium Assign dedicated resource; automate alerts; use robust hardware.
Indoor sensor deployment complexity Schools and public buildings may require permissions, IT support, or safeguarding considerations. Medium Medium Work with schools early; provide clear installation guidance.
Mobile sensor misuse or loss Atmotube devices may be misplaced or used inconsistently. Medium Low Provide training; assign devices to specific staff or schools.

4. Data Quality Risks

Risk Description Likelihood Impact Mitigation
Low‑cost sensor drift AirGradient and Atmotube sensors may drift without calibration. Medium Medium Pair with MCERTS sensors; periodic co‑location checks.
Indoor/outdoor data confusion Indoor sensors may be misinterpreted as ambient air quality. Medium Medium Clear labelling; separate dashboards for indoor vs outdoor.
Public misinterpretation of real‑time data Real‑time data may cause concern without context. Medium Medium Provide guidance notes; include health messaging; use thresholds.

5. Reputational Risks

Risk Description Likelihood Impact Mitigation
Perception of inaction If Lewisham does not expand monitoring, public may feel concerns are not addressed. Medium High Communicate improvements; publish dashboards; engage communities.
Over‑reliance on low‑cost sensors Public may question accuracy if low‑cost sensors dominate. Medium Medium Maintain MCERTS reference points; publish QA/QC approach.
Citizen science backlash Poor data quality or unclear messaging could undermine trust. Low Medium Provide training; use validated sensors; ensure transparency.

7. Technology‑Specific Risk Summary

MCERTS Sensors (Airly / Breathe London) - Strength: High accuracy, compliance‑grade
- Risk: High cost, annual maintenance, installation burden

AirGradient Outdoor - Strength: Very low cost, flexible, open‑source
- Risk: Not MCERTS; requires QA/QC

AirGradient Indoor - Strength: Affordable indoor monitoring
- Risk: Indoor readings may confuse public messaging

Airthings View Plus - Strength: Reliable indoor sensor with strong brand
- Risk: Higher cost; subscription features

Atmotube Mobile - Strength: Excellent for engagement and personal exposure studies
- Risk: Easy to lose; inconsistent use patterns

Cost–Benefit Summary: Lewisham Air Quality Monitoring Options

This summary compares the costs and benefits of expanding Lewisham’s air quality monitoring network using a mix of MCERTS sensors, low‑cost sensors, indoor monitors, mobile devices, and potential reductions in diffusion tube use. It incorporates all updated costs, including the contractor fee for changing diffusion tubes (£1,005.42/month).

1. Financial Summary

Current Annual Cost of Diffusion Tubes

  • Tubes + analysis: £7,344
  • Contractor (changing 162 tubes): £12,065
  • Total annual cost: £19,409

This is the baseline cost that could be partially or fully reallocated under Proposal 2.

Sensor Costs (Unit Prices)

Sensor Type Unit Cost Notes
MCERTS Outdoor (Airly) £4,085 (3‑yr) / £6,075 (5‑yr) +£350 annual maintenance
AirGradient Outdoor £175 Non‑MCERTS
AirGradient Indoor £179 Non‑MCERTS
Airthings View Plus (Indoor) £260 Indoor IAQ
Atmotube PRO (Mobile) £180 Personal exposure

Annual Savings from Tube Reduction

Tube Reduction Annual Saving
25% £4,852
50% £9,704
75% £14,556
100% £19,409

These savings can be reinvested directly into sensors.

2. Benefits Summary

MCERTS Outdoor Sensors (Airly / Breathe London)

Benefits - Compliance‑grade particulate monitoring
- High accuracy and reliability
- Strong alignment with Coroner’s concerns
- Suitable for public dashboards and alerts

Costs / Limitations - Very high capital cost
- Annual maintenance burden
- Installation/removal cost (~£350/year per unit)
- Best used sparingly at strategic locations

AirGradient Outdoor Sensors

Benefits - Extremely low cost
- Easy to deploy
- Open‑source and flexible
- Ideal for expanding spatial coverage
- Suitable for schools, community engagement, and hotspot mapping

Costs / Limitations - Not MCERTS
- Requires QA/QC and periodic co‑location
- Not suitable as standalone compliance evidence

Indoor Sensors (AirGradient Indoor / Airthings View Plus)

Benefits - Supports public health messaging
- Useful for schools, workplaces, vulnerable households
- Helps identify indoor pollution sources (cooking, heating, ventilation)
- Complements outdoor network

Costs / Limitations - Indoor readings must be clearly separated from ambient AQ data
- Higher unit cost (Airthings)
- Requires permissions and installation planning

Atmotube PRO Mobile Sensors

Benefits - Excellent for personal exposure studies
- Highly flexible and portable
- Ideal for citizen science, school projects, hotspot investigation
- Very low cost

Costs / Limitations - Not fixed-location monitoring
- Data consistency depends on user behaviour
- Devices can be lost or misused

3. Strategic Benefits by Proposal

Proposal 1 — Maintain tubes + add sensors (MAQF funding)

Benefits - Low operational disruption
- Retains statutory tube network
- Adds real‑time capability
- Incremental improvement

Limitations - Diffusion tubes remain dominant
- Limited alignment with Coroner’s concerns
- High recurring tube + contractor cost remains
- Less flexibility for future expansion

Proposal 2 — Reduce tubes + expand sensors + reinvest savings

Benefits - Strong alignment with Coroner’s concerns
- Major recurring savings (£4,852–£19,409/year)
- Enables rapid expansion of sensor network
- Supports public dashboards, school engagement, citizen science
- More granular temporal data (peaks, diurnal patterns, episodes)
- Flexible mix of MCERTS + low‑cost sensors

Limitations - Requires QA/QC strategy
- Requires careful planning for sensor deployment
- Indoor/mobile data must be clearly communicated

4. Cost–Benefit Conclusions

High‑Value Investments

  • AirGradient Outdoor: best cost–coverage ratio; ideal for borough‑wide expansion
  • Atmotube PRO: best for engagement and personal exposure studies
  • AirGradient Indoor: low‑cost indoor monitoring for schools and vulnerable groups

Strategic Investments

  • MCERTS sensors: essential for compliance and high‑confidence public alerts; should be deployed sparingly at key locations

Low‑Value Investments

  • Maintaining full diffusion tube network: high recurring cost (£19,409/year) with limited temporal resolution

Best Overall Approach

A mixed network combining:

  • a small number of MCERTS sensors
  • a large number of AirGradient outdoor sensors
  • targeted indoor sensors
  • mobile Atmotube devices for engagement
  • reduced diffusion tube network

This approach: - maximises spatial coverage
- improves real‑time public information
- reduces recurring costs
- aligns with Coroner’s concerns
- supports schools and communities
- maintains statutory compliance

Here’s a clear, concise, management‑ready recommendation section that follows naturally from your cost–benefit summary and prioritisation matrix. It is written in a professional, strategic tone suitable for an internal decision‑making document.

Suggestion

Based on the cost analysis, risk register, prioritisation matrix, and the Coroner’s concerns regarding the need for more granular, real‑time public information, the following suggestions are proposed for Lewisham’s air quality monitoring strategy.

1. Transition toward a sensor‑led monitoring network

Lewisham should begin a phased shift away from reliance on diffusion tubes and toward a mixed sensor network that provides higher temporal resolution, improved public accessibility, and greater flexibility. Diffusion tubes remain useful for long‑term trend analysis, but their limited temporal resolution and high recurring cost (£19,409/year including contractor fees) make them less suitable as the backbone of a modern monitoring system.

A reduction of 50–75% in tube numbers would release £9,704–£14,556 per year, enabling significant reinvestment in real‑time sensors.

2. Deploy a small number of MCERTS‑certified sensors at strategic locations

MCERTS sensors (Airly/Breathe London) provide MCERTS‑grade particulate data and should be used sparingly at key sites where:

  • high‑confidence public alerts are required
  • data will be used for statutory reporting
  • validation of low‑cost sensors is needed

A recommended deployment is 5–10 MCERTS sensors, balancing accuracy with cost.

3. Expand borough‑wide coverage using low‑cost outdoor sensors

AirGradient outdoor sensors offer the best cost‑coverage ratio and are easy to deploy across schools, residential areas, and suspected hotspots. They strongly support the Coroner’s concerns by enabling:

  • real‑time public dashboards
  • hyperlocal exposure information
  • identification of short‑term pollution episodes
  • community engagement

Savings from diffusion tube reduction could fund 50–100 AirGradient sensors, creating a borough‑wide network at minimal cost.

4. Introduce indoor monitoring in targeted settings

Indoor air quality is increasingly recognised as a public health priority. A small number of indoor monitors (AirGradient Indoor or Airthings View Plus) should be deployed in:

  • schools
  • council buildings
  • settings with vulnerable populations

This supports public health messaging and complements outdoor monitoring.

Recommended deployment: 10–20 indoor monitors.

5. Use mobile sensors (Atmotube PRO) for engagement and targeted studies

Mobile sensors provide valuable insight into personal exposure and are ideal for:

  • school projects
  • citizen science
  • hotspot investigations
  • short‑term studies

They are low‑cost and highly flexible. A recommended deployment is 20–50 Atmotube devices for community and educational use.

6. Develop a QA/QC and data integration framework

A mixed network requires a clear approach to:

  • calibration
  • co‑location checks
  • data validation
  • integration into dashboards
  • communication of indoor vs outdoor readings

This ensures public confidence and prevents misinterpretation.

7. Strengthen public communication and real‑time information access

To address the Coroner’s concerns, Lewisham should:

  • publish real‑time air quality dashboards
  • provide guidance on exposure reduction
  • promote awareness of UK‑Air and local monitoring tools
  • integrate sensor data into public‑facing platforms

Input from public health teams and data scientists will enable Lewisham make the best use of the data collcted. This will help residents make informed decisions during pollution episodes.

Overall Recommendation

Lewisham should adopt Proposal 2:
Reduce diffusion tube numbers and reinvest savings into a mixed sensor network, combining:

This approach:

It represents the most cost‑effective, future‑proof, and strategically aligned option for Lewisham’s air quality monitoring network.