Pictures: Great Smog of London London 1952

Accounts about air pollution date back to the 13th Century. Early occurrences resulted from:

  • Rapid population growth,
  • Urbanisation and changes in fuel use – the medieval switch from wood to coal, especially in brick kilns and domestic fireplaces was the main source of air pollution until the 1950s, then smoke and Sulphur Dioxide (SO2) the main pollutants.
  • Coal combustion in industrial furnaces, boilers
  • Domestic fireplaces. During calm, cold winter weather, pollutant concentrations could cause severe pollution episodes, termed smogs (smoke + fog), where the combination of smoke and SO2 emissions forms a thick fog, leading to serious health problems. Such pollution episodes occurred as early as the 17th century but, with rapid industrialisation became more frequent and more severe towards the end of the 19th century. Legislation at this time focused only on smoke abatement from industry, and difficulties in implementation led to little improvement in air quality until the early 20th century. Across the UK, episodes of extremely poor urban air quality occurred less frequent from around 1900, as industry and residential areas moved from the centre of cities. A trend towards using town gas and electricity also contributed although the use of coal in their production inevitably involved emissions somewhere. However, pollution episodes such as the Great Smog still occurred, and not only in London. This caused severe and widespread health impacts and great public concern leading to the Clean Air Acts of 1956 and 1968. These acts regulated domestic sources for the first time and introduced ‘smoke control areas’. The focus was purely on smoke from coal; SO2 emissions were not directly regulated, although subsequently, these dropped in parallel with smoke levels. Since the 1960s,
  • The burning of cleaner fuels (especially natural gas),
  • The decline in heavy industry and the location of power stations with high stacks outside cities has led to an over 90% decrease in national average smoke and SO2 levels.

The 1952 London major smog event led to approximately 12,500 deaths and substantial increases in respiratory illness.This public health toll was the most significant amongst the many reported smog events in London’s history that stretch back over many centuries.Its impacts on health were profound and such was the public response to the problem that political action to ensure it could not be repeated was inevitable. Private members bill, Beaver Committee whose recommendations ultimately resulted in the Clean Air Act, 1956.

Catastrophe drives action. Creates a willingness to act.
However good intentions fall foul of vested interests.

Source: University of West England; Bristol

The Clean Air 1965 Act demonstrated that substantial air quality improvements could be produced when concerted and sustained governmental action was directed at an environmental and public health problem.

The Act banned dark smoke emissions from:

  • Chimneys,
  • Railway engines and vessels,
  • Required new furnaces to be smokeless, required the emissions of grit and dust from furnaces to be minimised and gave local council’s powers to introduce smokeless zones.
  • The Clean Air Act helped the UK achieve a world leading position in the battle against air pollution.
  • However, the importance of sustained interest became apparent later on as elimination of “pea soupers” created a prevailing ideology that air pollution had been conquered.
  • Resources were directed towards other problems as governmental priorities changed.
  • Late 1980s and early 1990s – a growing public health concern related to childhood asthma and an association with traffic emissions.
  • The Environment Act of 1995 and the National Air Quality Strategy, 1997 provide the foundations for what promised to be a sustained and concerted attempt to manage air pollution and to reduce it below levels considered to be a risk to public health.
  • The onset of health-based concerns about the impacts of the growth of road traffic in the 1980s and 1990s left the UK woefully ill prepared to tackle a new form of air pollution.

Cause of Air Pollution

The biggest contributor to air pollution is road transport, however there are other sources as seen in the pictogram below which identifies which pollutant arises from each source (PM2.5, NO2, SO2, NMVOC)

However, the impact on air quality is indicative of high car ownership in Cheshire East with 40% of households having two or more cars against a UK average of 29%.

Source: CEC Transport Strategy 2019 – 2023

What should not be dismissed however is the issue of fugitive emissions from waste and other facilities. Consequently, this has been issue has been embedded into the Middlewich Town Council Air Quality Working Group Terms Of Reference.

The most significant harmful products from vehicle exhaust are;

1) Carbon monoxide (CO) Carbon monoxide results from the incomplete combustion where the oxidation process   does not occur completely.

2) Hydrocarbons (HC) Hydrocarbon emissions are composed of unburned fuels because of insufficient temperature which occurs near the cylinder wall

3) Particulate matter (PM) Particulate matter emissions in the exhaust gas are resulted from combustion process. Most particulate matters are resulted from incomplete combustion of the hydrocarbons in the fuel and lube oil.

4) Nitrogen oxides (NOx) Diesel engines use highly compressed hot air to ignite the fuel. Air, mainly composed of oxygen and nitrogen, is initially drawn into the combustion chamber.

5) Particulate Matter (PM-PM10 and PM2.5) Particulate Matter is generally categorised based on the size of the particles (for example PM2.5 is particles with a diameter of less than 2.5µm).

PM is made up of a wide range of materials and arise from a variety of sources. Concentrations of PM comprise primary particles emitted directly into the atmosphere from combustion sources and secondary particles formed by chemical reactions in the air. PM derives from both humanmade and natural sources (such as sea spray and Saharan dust).

In the UK, the biggest human-made sources are stationary fuel combustion and transport. Road transport gives rise to primary particles from engine emissions, tyre and brake wear and other non-exhaust emissions. Other primary sources include quarrying, construction, and non-road mobile sources.

Secondary PM is formed from emissions of ammonia, Sulphur dioxide and oxides of nitrogen as well as from emissions of organic compounds from both combustion sources and vegetation.

6) Oxides of nitrogen (NOX) All combustion processes in air produce oxides of nitrogen (NOX). Nitrogen dioxide (NO2) and nitric oxide (NO) are both oxides of nitrogen and together are referred to as NOX.

Road transport is the main source, followed by the electricity supply industry and other industrial and commercial sectors.

7) Ozone (O3) Ozone is not emitted directly from any humanmade source. It arises from chemical reactions between various air pollutants, primarily NOX and Volatile Organic Compounds (VOCs), initiated by strong sunlight. Formation can take place over several hours or days and may have arisen from emissions many hundreds, or even thousands of kilometres away.

8) Sulphur dioxide (SO2) UK emissions are dominated by combustion of fuels containing Sulphur, such as coal and heavy oils by power stations and refineries. In some parts of the UK, notably Northern Ireland, coal for domestic use is a significant source.

9) Polycyclic aromatic hydrocarbons (PAHs) There are many different PAHs emanating from a variety of sources. This strategy uses benzo[a]pyrene (B[a]P) as a marker for the most hazardous PAHs.

The main sources of B[a]P in the UK are domestic coal and wood burning, fires (e.g. accidental fires, bonfires, forest fires etc.), and industrial processes such as coke production. Road transport is the largest source for total PAHs, but this source is dominated by species thought to be less hazardous than B[a]P

10) Benzene Has a variety of sources, but primarily arises from domestic and industrial combustion and road transport.

11) 1,3-butadiene Mainly from combustion of petrol. Motor vehicles and other machinery are the dominant sources, but it is also emitted from some processes, such as production of synthetic rubber for tyres.

12) Carbon monoxide (CO) Formed from incomplete combustion of carbon containing fuels. The largest source is road transport, with residential and industrial combustion making significant contributions.

THE EFFECTS ON HEALTH THROUGH POOR AIR QUALITY

In the UK about 29000 deaths per year are associated with exposure to fine particles, Particulate Matter, (PM2.5), ca. 5-6% of total deaths.

In cities PM2.5 primarily comes from cars, lorries and buses but they are also produced by the burning of wood, heating oil or coal for domestic or industrial purposes. In Europe, the WHO estimates about 500,000 people die prematurely as a result of air pollution every year. These estimates do not include any contribution from NO2.

It is estimated that the effects of NO2 on mortality are equivalent to 23,500 deaths annually in the UK (but heavily caveated). Many of the sources of NOx (NO2 and NO) are also sources of particulate matter (PM).

The combined impact of these two pollutants maybe as much as 52 000 deaths per year and represents a significant public health challenge.

The response to this burden is inadequate to say the least

Source: Committee on the Medical Effects of Air Pollutants (COMEAP)

Focus on health impacts of continuous exposure to chronic air pollution over a lifetime, with specific reference to:

  • Pregnancy, children, and adults
  • indoor and outdoor exposure
  • the influence of local, regional, and national policy relating to pollution control measures
  • examining the influences of climate change
  • socio-economic impacts of air pollution.

Estimate 40000 premature deaths annually from PM and NO2 in the UK, this is slightly less than other estimates.

Source: RCP/RCPH Report (Feb 2016)

As can be seen from the pictogram, particulate matter is extremely small, and with the addition of the NO2 fumes they are both easily absorb into the body. When air pollutants enter the body, they can have effects on various organs and systems, not just the respiratory system.

This includes:

  • The lungs and respiratory system
  • The eyes, nose, and throat
  • The heart – heart and blood vessel diseases, including strokes and hardening of the arteries, are one of the main effects of air pollution

There is evidence emerging suggesting air pollution may also affect the brain and is linked, potentially, to dementia and cognitive decline. Additionally, associating air pollution with early life effects such as low birth weight.

Source: Public Health England

HEALTH ISSUES SPECIFIC TO MIDDLEWICH

Focusing on the health issues in Middlewich, CEC publish a spreadsheet called the ‘Health Profiles for Electoral Wards plus Primary Health and Social Care Areas’, last updated 2017. (Commonly named as the Tartan Rug)

Appendix B – ward quintile analysis jul 15.pdf (cheshireeast.gov.uk)

Quantile1 being highest 20% of wards nationally to Quantile 5 being Lowest 20% of wards nationally. Although these statistics cannot and should not be directly attributable to poor air quality, it should be considered

  • Emergency admissions for respiratory is Quantile 2
  • New cases lung cancer is Quantile 1
  • Heart deaths under 75 is Quantile 1
  • Deaths from respiratory disease is Quantile 2”

THE LAW

The Clean Air Strategy was published was published in January 2019. The foreword by the Secretary of State for Environment, Food and Rural affairs (Defra) identifies air pollution as the top environmental risk to human health in the UK. 

The Clean Air Strategy should be seen as part of a suite of policy documents sets out the case for action to improve UK air quality. The strategy is focused on tackling air pollution in England but also highlights action being taken in Northern Ireland, Scotland and Wales.

There has been plenty of guidance, but has it been effective in delivering cleaner air?

Without question it has helped to identify where poor air quality exists, but has it led to cleaner air?                                                                                        

Source: University of West England; Bristol

The UK Government and EU have set legally binding Limits on NO2 and PM. It should be noted that DEFRA is in a consultation process aligned to the Environmental Bill, currently passing through Parliament reviewing the concentrations limits of Particulate Matter.

Click here to view the National air quality objectives and European Directive limit and target values for the protection of human health

Cheshire East Council Policies

CEC has a statutory duty under the Environment Act 1995 (Part IV) to have Local Air Quality Management plans and to regularly review both the current and future air quality within its areas. The plans and reviews must follow Government guidance that sets health-based objectives, which are considered to be acceptable given the known effects of poor air quality. On the whole CEC believes the air quality across most of the borough is good; however, there are a number of small areas where, due to traffic, there are concerns about nitrogen dioxide.

Source: CEC Local Air Quality Management

Every year CEC publishes an Annual Quality Status Report which covers the following topics

  • Executive summary
  • Local Air Quality management
  • Actions to improve air quality
  • Air Quality Monitoring Data and Comparisons with Objectives
  • Monitoring Results

The latest (2020) Annual Quality Status Report can be found at ASR 2020 (cheshireeast.gov.uk)

CEC Methodology and Monitoring Air Quality in Middlewich

CEC currently monitor nitrogen dioxide and (at a small number of sites) utilising benzene Palmes Diffusion tubes. The diffusion tubes work by passively absorbing the NO2 pollutant to which they are exposed to in each place over a given time.  There are no pumps or complicated technologies involved; tubes are exposed, normally for a month, resealed and sent to a laboratory.

Diffusion tubes are a relatively cheap, convenient and pollutant specific method of monitoring many different types of air pollution.  The tubes are small and can be located exactly where they need to monitor.

Source: CEC (Sept 2019)

They are useful for providing longer term measurements and observing trends in pollution concentrations. Tubes can be placed on the outside of buildings, or suitably located street furniture (road signs, or lamp posts) around the Borough.

The laboratory then completes the analysis of the tubes using nationally agreed procedures. The monthly results are then adjusted at the end of the year to take account of laboratory and other inaccuracies, and a single annual mean figure is produced.

This figure is used for the purposes of review and assessment and comparison with the Air Quality Objective.

The convenience of diffusion tubes comes with three main disadvantages.

  • Primarily for monitoring NO2, not direct measuring of PM
  • The main disadvantage is accuracy (the results are considered to be +/- 20% accurate),
  • and of course, you only get one number representing a whole month, meaning it is not possible to examine daily or weekly fluctuations. 

Sources: Cheshire East Council:      

Diffusion Tubes for Ambient NO2 Monitoring: Practical Guidance for Laboratories and Users Report to Defra and the Devolved Administrations

The results of the monthly NO2 diffusion tube monitor is found in ‘datasets’ published on the CEC Air Quality Website.

The latest dataset are reviewed by the AQWG and areas of concern are raised with the relevant  CEC Officer(s) to repositioned or introduce diffusion tubes

The importance of clean air cannot and should not be underestimated. Since the beginning of the Industrial Revolution in the UK and throughout the world it has been known that poor air quality has a detrimental effect on our health and the environment, both short and long term.

The pictorial (1) on the left sums ups quite succinctly the scale of the problem of poor air quality in the UK.

The pictorial also demonstrates what can be achieved with the reduction of 1 ug/m³ in fine particulate matter.

Tubes can be placed on the outside of buildings, or suitably located street furniture (road signs, or lamp posts) around the Borough. 

Locations are selected on the pictorial criteria. Full details about Cheshire East Councils work on local Air Quality can be viewed here:

Cheshire East Council Air Quality