37
experienced by householders. The key finding of EST’s 2009 field trial of condensing gas
boilers was that the efficiency of condensing boilers at home was typically 5 percent less than
published SEDBUK ratings
. An efficiency of 85% is therefore assumed in the economic model
for calculation of CO
2
emissions.
CO
2
emissions from heat sources
The CO
2
intensity of heat from a range of heat networks and counterfactual technologies can be
compared to provide an indication of the relative performance of each technology. Figure 3
overleaf, shows the CO
2
intensity of heat supplied from different technologies for a range of
different electricity grid CO
2
intensities. For technologies which either consume electricity or
generate electricity, the CO
2
intensity of heat varies with the electricity emission factor. The
current average electricity grid CO
2
emissions factor is circa 0.54 kg CO
2
/ kWh
. Figure 3
demonstrates that if electricity from gas fired CHP is assumed to displace grid electricity at this
intensity it can deliver heat at a negative CO
2
intensity, and is the lowest carbon form of heat
generation of all technologies shown. This assumes that the electricity generated from the CHP
unit is valued at the same CO
2
intensity as electricity supplied to other technologies. In heat
network schemes, the CHP plant will only be providing a proportion of the heat, with the
remainder from gas boilers. This, in combination with distribution losses, means that a negative
CO
2
emissions factor for heat is unlikely to be achieved in practice. The chart assumes a gas
boiler efficiency of 85%, and CHP efficiencies of 37% electrical and 40% thermal (as indicated
in the key).
As the electricity CO
2
emissions factor reduces, the heat CO
2
emissions factor from gas fired
CHP increases due to the reduced benefit of displacing grid electricity. Below a grid emissions
factor of 0.5 kg CO
2
/ kWh, heat from biomass boilers becomes the lowest carbon source, but
CHP remains lower carbon than heat pumps until the grid emissions factor reduces to around
0.35 kg CO
2
/ kWh. For gas boilers or direct electric heating to become lower carbon than gas
fired CHP, the grid emissions factor needs to reduce to circa 0.2 kg CO
2
/ kWh.
However, comparisons between different heat sources are complicated by the fact that grid
emissions factors for electricity displaced by CHP will not be the same as grid emissions factors
for electricity consumed in electrode boilers and heat pumps. The carbon intensity of electricity
displaced by CHP will depend upon its operating costs in comparison to the cost of power from
other generation types, the proportion of the CHP’s output which is sold to the wholesale market
versus that used locally displacing retail price electricity and the extent to which the CHP is
embedded within the distribution network. LCP have recently modelled
competition of gas
CHP with other generating capacity for DECC including modelling the effect of these issues.
This work concluded that, on average, under DECC’s central grid decarbonisation trajectory
operation of gas CHP will continue to deliver annual carbon savings until 2032.
http://www.energysavingtrust.org.uk/northernireland/Organisations/Technology/Field-trials-and-monitoring/Field-
trial-reports/Condensing-boilers-and-advanced-room-thermostats-field-trials
DEFRA UK Government Conversion factors for company reporting. Generation average of 0.494 kg/kWh, and
transmission and distribution losses of 0.0432 kg/kWh, providing a total supplied factor of 0.537 kg/kWh.
https://www.gov.uk/government/uploads/system/uploads/attachment_data/file/389070/LCP_Modelling.pdf