Guidance

Forthcoming change: appraisal updates

Updated 16 April 2026

Description: we are updating the economic and demographic parameters for appraisal data, and improving the way we communicate changes to users

Unit: TAG data book, TAG unit A3 (environmental impact appraisal)

Change announced: April 2026

Expected release date: May 2026

Updates to economic and demographic data

The TAG data book provides a range of economic and demographic datasets used in the appraisal of transport interventions. To maintain the accuracy of appraisals, these data sets are updated in line with new releases of data from the Office for National Statistics (ONS) and Office for Budget Responsibility (OBR).

A new version of the TAG data book (v2.03), to be released definitively in May 2026, will incorporate the latest 5-year medium-term forecasts from the OBR’s March 2026 economic and fiscal outlook (EFO), as well as 2025 outturn data from the ONS.

The figures from the ONS and the EFO will be used to update the parameters in the data book’s annual parameters tab, table A1.2.1 (cost inflation series) and table A5.3.1 (inflation measures and real average earnings index).

The OBR’s economic forecasts have changed minimally since November 2025, so we expect little impact from this update.

Those appraisal workbooks that utilise the annual parameters table for price adjustments, discounting and uprating will also be updated accordingly. The relevant workbooks are:

  • greenhouse gases
  • air quality
  • landscape monetisation
  • noise
  • noise (aviation)
  • active mode appraisal toolkit
  • cost proforma

Clarification to values of time per person in the data book

In the notes section of table A1.3.1 (values of time per person) of the TAG data book, we will clarify that the values of travel time per person in that table are uplifted in future years at a constant 1.5% per annum (real terms) in appraisal. The note reflects current guidance in TAG unit A1.1.

Updating the marginal external cost (MEC) of congestion

As we announced in the road freight values of travel time forthcoming change, we are planning to update tables A5.4.2 and A5.4.4 (marginal external cost of congestion) in the data book, using updated NTM runs. While we were hoping to release these in May 2026, these changes are now delayed to allow for greater assurance around the updates.

Updates to air quality damage costs

The Department for Environment, Food and Rural Affairs (Defra) has updated the appraisal values of air quality damage. Some of these metrics are reported in table A3.2 (air quality) of the TAG data book.

The national central values (best estimates) for NOx and PM2.5 damage costs have increased by 9% and 34%, respectively. The updated damage costs reflect changes in the underlying methodology and inputs used to calculate them:

  • emission and ambient measurement data
  • the dispersion modelling for NOx and PM
  • underlying trends in mortality rates, population and inflation

We are also updating the factors to convert PM10 emissions to PM2.5 emissions.

The tables below show the updated damage costs for NOx and PM2.5 (in 2023 prices and 2023 values) and the updated factors to convert PM10 emissions to PM2.5 emissions.

Table: damage cost values for NOx in £ per tonne

Central value sensitivities Low value sensitivities High value sensitivities
NOx national 9,337 1,531 31,644
NOx aircraft 15,729 2,149 54,544
NOx rail 12,129 1,801 41,645
NOx ships 3,319 949 10,086
NOx road transport 12,486 1,836 42,926
NOx road transport central London 66,626 7,072 236,880
NOx road transport inner London 65,601 6,973 233,209
NOx road transport outer London 36,684 4,176 129,613
NOx road transport inner conurbation 26,497 3,190 93,118
NOx road transport outer conurbation 16,822 2,255 58,461
NOx road transport urban big 16,172 2,192 56,131
NOx road transport urban large 13,105 1,895 45,145
NOx road transport urban medium 10,653 1,658 36,360
NOx road transport urban small 9,171 1,515 31,051
NOx road transport rural 5,445 1,154 17,700
NOx rail transport central London 76,493 8,028 272,228
NOx rail transport inner London 73,820 7,770 262,649
NOx rail transport outer London 47,275 5,204 167,549
NOx rail transport inner conurbation 28,861 3,423 101,581
NOx rail transport outer conurbation 15,785 2,159 54,732
NOx rail transport urban big 16,556 2,234 57,490
NOx rail transport urban large 13,210 1,912 45,504
NOx rail transport urban medium 10,018 1,603 34,067
NOx rail transport urban small 8,122 1,421 27,273
NOx rail transport rural 5,459 1,164 17,729

Table: damage cost values for PM2.5 in £ per tonne

Central value sensitivities Low value sensitivities High value sensitivities
PM2.5 national 104,799 36,663 340,431
PM2.5 aircraft 134,415 46,792 407,144
PM2.5 rail 102,366 35,440 285,142
PM2.5 ships 60,174 20,814 165,268
PM2.5 road transport 111,038 38,751 348,559
PM2.5 road transport central London 593,662 207,281 1,876,312
PM2.5 road transport inner London 575,727 201,136 1,834,442
PM2.5 road transport outer London 323,550 113,017 1,028,711
PM2.5 road transport inner conurbation 232,306 81,093 731,798
PM2.5 road transport outer conurbation 145,733 50,859 457,566
PM2.5 road transport urban big 140,026 48,874 440,333
PM2.5 road transport urban large 112,560 39,285 353,678
PM2.5 road transport urban medium 91,268 31,854 286,765
PM2.5 road transport urban small 77,857 27,172 244,497
PM2.5 road transport rural 45,059 15,721 140,982
PM2.5 rail transport central London 511,526 176,889 1,399,229
PM2.5 rail transport inner London 650,313 224,882 1,778,675
PM2.5 rail transport outer London 418,324 144,661 1,144,447
PM2.5 rail transport inner conurbation 243,780 84,301 666,841
PM2.5 rail transport outer conurbation 132,907 45,965 364,223
PM2.5 rail transport urban big 145,454 50,302 398,313
PM2.5 rail transport urban large 109,698 37,967 304,178
PM2.5 rail transport urban medium 81,946 28,349 225,554
PM2.5 rail transport urban small 67,154 23,256 188,015
PM2.5 rail transport rural 42,015 14,557 118,539
PM10 to PM2.5 conversion factors
National (all sectors) 0.506
Aircraft 0.636
Rail (RaT) 0.888
Ships 0.947
Road transport (RoT) 0.564
RoT central London 0.551
RoT inner London 0.537
RoT outer London 0.541
RoT inner conurbation 0.557
RoT outer conurbation 0.563
RoT urban big 0.561
RoT urban large 0.562
RoT urban medium 0.562
RoT urban small 0.563
RoT rural 0.570
RoT exhaust 1.000
RoT brake 0.400
RoT tyre 0.710
RoT road abrasion 0.545
RaT central London 0.966
RaT inner London 0.966
RaT outer London 0.965
RaT inner conurbation 0.966
RaT outer conurbation 0.957
RaT urban big 0.961
RaT urban large 0.906
RaT urban medium 0.938
RaT urban small 0.868
RaT rural 0.839

We are also updating table A3.2.2 by presenting concentration based damage cost values for NOx and PM2.5 from table 7-9 of the research report underlying the damage cost update.

Table: costs per µgm-3 concentration change (2025 prices, 2025 values) – central damage costs sensitivity

Primary pollutant A) Direct impacts (£ per popwm 1 µgm-3 change per person per year) B) Secondary PM2.5 impacts (£ per tonne) C) Other impacts (£ per tonne)
NOx 8.58 2,780 -12
PM2.5 65.95 - -

We will add the following methodological note to accompany table A3.2.2:

Damage costs are typically expressed per tonne of emission. However, costs can also be expressed for many of the damage cost pathways per µgm-3, which is the unit of concentration. The costs per change in concentration need to be multiplied by the population weighted change in concentration, and the total population in the appraisal domain to estimate the total cost.

Not all impacts which make up the damage costs are calculated based on concentration exposure. As such, where the costs per change in concentration are deployed to estimate effects, analysts will also need to calculate the costs for additional ‘other impacts’ that are expressed per tonne. These ‘other impacts’ costs include pathways to assess environmental, productivity, and building impacts, and are separate to, and thus do not overlap with those included as ‘direct impacts’.

The ‘direct impacts’ (column A) and ‘other impacts’ (column C) cost estimates can be added together to generate the total cost estimate if the formation of secondary PM2.5 has been included in the air pollution modelling (A+C).

If the formation of secondary PM2.5 has not been included in the air pollution modelling, then the ‘direct impacts’ (column A), ‘secondary PM2.5 impacts’ (column B) and ‘other impacts’ (column C) cost estimates should be added together to generate the total cost estimate (A+B+C).

We will add the following sentence to paragraph 3.2.5 of TAG unit A3 (environmental impact appraisal):

If you use this table, please contact Defra at igcb@defra.gov.uk to receive further guidance.

Improving how we communicate changes to users

We are making it easier for users to understand what has changed in TAG after each publication cycle by:

  • including links to the archived forthcoming changes when we email users about the definitive changes being available
  • publishing online an overview spreadsheet with links to the previous versions of TAG
  • ensuring the ‘provenance’ section of each TAG unit is kept up to date for any future changes

Contact

For further information on this guidance update, please contact:

Transport Appraisal and Strategic Modelling (TASM) division
Department for Transport
Zone 1/3 Great Minster House
33 Horseferry Road
London
SW1P 4DR

Email: tasm@dft.gov.uk