Page 8 - Swale AQMA Feasibility Study April 2020_
P. 8

AQMA Feasibility Assessment
               A2 – Keycol Hill and Key Street, Swale



                 2.6    Being background concentrations, the UK-AIR data are intended to represent a
                        homogenous  mixture  of  all  emissions  sources  within  the  general  area  of  a
                        particular  grid  square  location.  Concentrations  of  pollutants  at  various
                        sensitive  receptor  locations  can,  therefore,  be  calculated  by  modelling  the
                        emissions  from  a  nearby  pollution  source,  such  as  a  busy  road,  and  then
                        adding this to the appropriate UK-AIR background datum.

                 2.7    In order to determine the  baseline air quality conditions for 2018, emissions
                        from local roads have been assessed using a detailed air dispersion model. The
                        model used was ADMS-Roads (version 4.1), which is produced by CERC and has
                        been  validated  and  approved  by  Defra  for  use  as  an  assessment  tool  for
                        calculating  the  dispersion  of  pollutants  from  traffic  on  UK  roads.  The  latest
                                                              6
                        Defra  Emissions  Factor  Toolkit  (EFT)   was  used  within  the  model  to  estimate
                        vehicle emissions.
                 2.8    Detailed,  hourly  sequential,  meteorological  data  are  used  by  the  model  to
                        determine  pollutant  transportation  and  levels  of  dilution  by  the  wind  and
                        vertical air movements. Meteorological data used in the model were obtained
                        from Gravesend as it was considered to provide the most representative data
                        of  similar  conditions  to  the  site.  The  meteorological  data  used  for  this
                        assessment were from 2018, for which air quality monitoring and traffic data
                        were also available. The surface roughness applied to the model for the site
                        was 0.75m. A factor of 0.1m was applied to the meteorological site.

                 2.9    Receptor  locations  are  indicated  in  Figure  1.  Discrete  model  receptors  were
                        positioned  at  the  façades  of  buildings  closest  to  the  source  of  pollution  (i.e.
                        roads).  Receptors  were  modelled  at  “breathing  height”,  which  was  1.5m  for
                        most locations. Receptors are, therefore, positioned in worst-case locations, for
                        a conservative approach. The locations were agreed with SBC’s Environmental
                        Health Department.

                 2.10   Details of sensitive receptors are included in Table 2.1, below.

                        Table 2.1: Modelled Receptors


                                                                           UK Grid Reference
                            Receptor      Location     Height (m)
                                                                          X               Y


                               R1         Keycol Hill      1.5         586912.88       164518.86

                               R2         Keycol Hill      1.5         586983.25       164518.02


                               R3         Keycol Hill      1.5         587115.88       164473.28

                               R4         Keycol Hill      1.5         587150.88       164480.88



               6 Defra (2017). Emissions Factor Toolkit v9.0.


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