Authors | Ben Fowler |
Compilation date | 18 April 2024 |
Customer | Spelthorne Borough Council |
Approved by | Louisa Kramer |
Copyright | Ricardo Energy & Environment |
EULA | http://ee.ricardo.com/cms/eula/ |
Contract reference | ED15866 | Report reference | ED15866101 |
This is an annual summary report for Spelthorne Borough Council covering the period 01/01/2023 - 31/12/2023.
This is a dynamic report which contains the data it displays embedded within and allows the reader a level of interaction with some of the findings. This enables a more easily navigated and streamlined report with a more engaging, intuitive reader experience.
Maps, tables and some plots have an element of interactivity to them which makes them easier to read or offers additional insight. Maps for example can be panned and zoomed with different layers and markers turned on and off and with popup information by clicking on markers or hovering the mouse over them. Tables may contain much more information than initially displayed and can be set to show different numbers of rows, and can be filtered sorted or searched to display only specific information of interest. Some time series plots can be tracked with the mouse cursor to obtain specific time/date stamps and values and the reader can zoom into a specific time window by dragging with the cursor and double left clicking to return to the full plot extent.
The report is easily navigable using the floating table of contents on the left pane which tracks with the reader’s progress through the report and expands and collapses to a level of detail related to the subheadings used. The layout of the report is also dynamic, with some sections split into specific ‘tabs’ (e.g. per pollutant or per site) for ease of access to those sections.
A summary of site information is presented in the interactive map and table below .
Figure 1: Location of sensor monitoring sites in Spelthorne
NO2 is a gas that is mainly formed from combustion processes such as wood burning wood and vehicle emissions. When breathed in NO2 can irritant the throat and lungs and worsen symptoms in those with underlying respiratory issues. NO2 is also involved in the formation of photochemical smog and acid rain and may cause damage to crops and vegetation.
Particulate matter in the atmosphere has many man-made and natural sources, and can vary widely in its physical and chemical composition, and size. For air quality PM is typically classified into two sizes - PM10 is the concentration of particles with an effective median diameter of 10 micrometers (μm) and PM2.5 the concentration of particles with an effective median diameter of 2.5 μm. PM2.5 is sometimes known as “fine” particulate matter. Fine particulate matter is a particular concern to human health, as the particles are small enough to penetrate deep into the lungs.
The table below shows the legal limits for NO2 and PM for local authorities in England as set out in the Air Quality Standards Regulations 2010. Also shown are the 2021 WHO guidelines.
The Daily Air Quality Index (DAQI) provides information on air pollution levels, recommended actions, and health advice. The index is numbered 1-10 and divided into four bands, low (1) to very high (10). More information on the AQ Index can be found on the Defra UK AIR website.
Band | DAQI | O3 | NO2 | PM2.5 | PM10 |
---|---|---|---|---|---|
Low | 1 | 0-33 | 0-67 | 0-11 | 0-16 |
2 | 34-66 | 68-134 | 12-23 | 17-33 | |
3 | 67-100 | 135-200 | 24-35 | 34-50 | |
Moderate | 4 | 101-120 | 201-267 | 36-41 | 51-58 |
5 | 121-140 | 268-334 | 42-47 | 59-66 | |
6 | 141-160 | 335-400 | 48-53 | 67-75 | |
High | 7 | 161-187 | 401-467 | 54-58 | 76-83 |
8 | 188-213 | 468-534 | 59-64 | 84-91 | |
9 | 214-240 | 535-600 | 65-70 | 92-100 | |
Very High | 10 | 241 or more | 601 or more | 71 or more | 101 or more |
AP Band | Accompanying health messages for at-risk individuals | Accompanying health messages for the general population |
---|---|---|
Low (1-3) | Enjoy your usual outdoor activities. | Enjoy your usual outdoor activities. |
Moderate (4-6) | Adults and children with lung problems, and adults with heart problems, who experience symptoms, should consider reducing strenuous physical activity, particularly outdoors. | Enjoy your usual outdoor activities. |
High (7-9) | Adults and children with lung problems, and adults with heart problems, should reduce strenuous physical exertion, particularly outdoors, and particularly if they experience symptoms. People with asthma may find they need to use their reliever inhaler more often. Older people should also reduce physical exertion. | Anyone experiencing discomfort such as sore eyes, cough or sore throat should consider reducing activity, particularly outdoors. |
Very High (10) | Adults and children with lung problems, adults with heart problems, and older people, should avoid strenuous physical activity. People with asthma may find they need to use their reliever inhaler more often. | Reduce physical exertion, particularly outdoors, especially if you experience symptoms such as cough or sore throat. |
The following tables present some basic pollutant statistics for the period selected in the report.
Figure 2: NO2 exceedence.
The plots below show the time series of concentrations each hour. Each pollutant is presented on a different tab and all sites are shown on each plot for comparison.
The plot is interactive and you can change what is shown by the following:
Figure 3: Time series plot of hourly average NO2 concentration.
Figure 4: Time series plot of daily average NO2 concentration.
Figure 5: Time series plot of hourly average PM2.5 concentration.
Figure 6: Time series plot of daily average PM2.5 concentration.
Figure 7: Time series plot of hourly average PM10 concentration.
Figure 8: Time series plot of daily average PM10 concentration.
The plots below show how the concentrations vary with hour of the day and day of week. These plots often help explain variations in concentration according to the emissions activity associated with them. For example, NO2 concentrations at roadside locations tend to show peaks in the morning and afternoon traffic rush hours and tend to decline over weekends when there is generally lower traffic volumes. For PM2.5 a peak often occurs later in the evening, which is likely due to emissions from domestic burning of wood for heating.
Similar to the the time series plots above, this plot is interactive. To select one site, double click on the site in the legend. Further sites can then be added with a single click. To return to all sites, double click again on the legend.
Figure 9: Time variation of hourly NO2 concentrations.
Figure 10: Time variation of hourly PM2.5 concentrations.
Figure 11: Time variation of hourly PM10 concentrations.
The plots below show daily variation in concentrations by pollutant and site (one on each tab) across the period of the report, as laid out in a calendar style. This allows intuitive viewing of day to day headline trends in the wider context of the period. The background colours shown for each day relate to the concentration. The actual concentrations, along with the wind speed, can also be seen by hovering the mouse on the cell.
Figure 12: PM10 calendar plot.
Figure 13: PM10 calendar plot.
Figure 14: PM10 calendar plot.
Figure 15: PM10 calendar plot.
Figure 16: PM10 calendar plot.
Figure 17: PM10 calendar plot.
Figure 18: NO2 calendar plot.
Figure 19: NO2 calendar plot.
Figure 20: NO2 calendar plot.
Figure 21: NO2 calendar plot.
Figure 22: NO2 calendar plot.
Figure 23: NO2 calendar plot.
Figure 24: PM2.5 calendar plot.
Figure 25: PM2.5 calendar plot.
Figure 26: PM2.5 calendar plot.
Figure 27: PM2.5 calendar plot.
Figure 28: PM2.5 calendar plot.
Figure 29: PM2.5 calendar plot.
The back trajectory plot shows data from the HYSPLIT model run in analysis mode. This shows the air mass back trajectories for the period covered by the report. Three different kinds of plot are shown. One statistically groups the trajectories into similar clusters and shows the proportion of time during the report period that each represents. This is useful to get an overview of air mass origins during the report period. On additional tabs, the trajectories associated with exceedances of the limit value (24-hr for PM10) is shown. A plot of the trajectories associated with the top 10 measured concentrations is also presented.
4-day air mass back trajectories arriving at London for 2023 are grouped into 6 clusters.
There were no NO2 hourly exceedances.
Trajectories for days when there was an exceedence in PM10 concentration are plotted below.
The average daily concentration for each pollutant across all the sites was calculated. The top 10 most polluted days were identified and linked to the back trajectory data.
The plot below shows bivariate plots, ‘’pollution roses’’ of hourly mean pollutant concentrations against the corresponding wind speed and wind direction. These plots should be interpreted as follows:
The wind direction is indicated as in the wind rose above (north, south, east and west are indicated).
The wind speed is indicated by the distance from the centre of the plot: the concentric circles indicate wind speeds in 5 ms-1 intervals.
The pollutant concentration is indicated by the colour (as indicated by the scale).
These plots therefore show how pollutant concentration varies with wind direction and wind speed.
The plots do not show distance of pollutant emission sources from the monitoring site. However, in the case of primary pollutants such as NO, the concentrations at very low wind speeds are dominated by emission sources close by, while at higher wind speeds, effects are seen from sources further away.
Name | Ben Fowler |
Address | Ricardo Energy & Environment, Gemini Building, Harwell, Didcot, OX11 0QR, United Kingdom |
Telephone | 01235 753554 |
ben.fowler@ricardo.com |