A COMPARISON OF BUILDING ENERGY EFFICIENCY STANDARDS BETWEEN UK AND CHINA
A Comparison of Building Energy Efficiency Standards between UK and China
Table of Contents
4.2. Comparison of total costs across the scenarios7
4.2.1. Exclusion of carbon emission cost7
4.2.2. Inclusion of carbon emission cost10
5. CONCLUDING REMARKS13
Table 4.
Gas-fired district boiler (heat only).
2006
2015
2025
GWh
1000 t C
GWh
1000 t C
GWh
1000 t C
TJ-97
3225
172
3573
191
4042
216
TJ-WB97
2896
155
3211
171
3644
195
TJ 2004
2568
137
2850
152
3247
173
TJ-WB04
2479
132
2753
147
3140
168
TJ-CAN
2431
130
2700
144
3082
165
TJ-RT2005
2273
121
2526
135
2891
154
TJ-SWE
2061
110
2279
122
2605
139
Table 5.
Gas-fired district small CHP.
2006
2015
2025
GWh
1000 t C
GWh
1000 t C
GWh
1000 t C
TJ-97
3741
100
4147
112
4688
128
TJ-WB97
3356
95
3724
105
4223
120
TJ 2004
2989
89
3321
98
3779
111
TJ-WB04
2868
88
3187
96
3633
109
TJ-CAN
2812
87
3127
95
3566
108
TJ-RT2005
2602
84
2895
92
3312
103
TJ-SWE
2341
80
2586
87
2948
96
Table 6.
Municipal large CHP.
2006
2015
2025
GWh
1000 t C
GWh
1000 t C
GWh
1000 t C
TJ-97
5266
163
5803
197
6500
242
TJ-WB97
4706
146
5188
177
5823
217
TJ 2004
4171
129
4600
157
5177
193
TJ-WB04
3994
124
4406
150
4964
185
TJ-CAN
3914
121
4318
147
4867
181
TJ-RT2005
3607
112
3981
135
4496
168
TJ-SWE
3228
100
3531
120
3966
148
Table 7.
Individual gas boiler.
2006
2015
2025
GWh
1000 t C
GWh
1000 t C
GWh
1000 t C
TJ-97
2227
119
2453
131
2755
147
TJ-WB97
2011
107
2216
118
2493
133
TJ 2004
1804
96
1989
106
2244
120
TJ-WB04
1736
93
1914
102
2161
115
TJ-CAN
1705
91
1880
100
2124
113
TJ-RT2005
1586
85
1750
93
1981
106
TJ-SWE
1440
77
1575
84
1776
95
Note: Primary energy demand consumed for electricity generation in CHP is not subtracted in Table 2, Table 3, Table 4, Table 5, Table 6 and Table 7, this explain why CHPs have higher primary energy supply.
However, prudence is necessary when interpreting the difference between the energy supply options. First, the scenario of individual gas boiler option appears to be the best scenario in terms of primary energy savings, but it disguises the fact that electricity is also generated in all the scenarios with cogeneration option. Indeed, the primary demand in heat-only scenarios must be much higher if upstream energy consumption for electricity generation is taken into account. Second, gas-fuelled energy supply system appears to be preferred to coal-fired district heating if the primary objective is the CO2 emission mitigation. However, fuel-switching policy should be assessed much more deeply than just comparing the carbon emission outcome, the economic dimension should not be ignored. More convincing decision on investment strategies can be made through the insights in the analysis of costs in Section 4.2.
4.2. Comparison of total costs across the scenarios
All costs incurred in buildings and energy supply over the modelling are discounted to the base year (2006) and are accounted for as yuan/m2 floor space to harmonise the criteria for comparison, since the unitary incremental cost related to BEE measures is expressed systematically in buildings construction programme. Cost scenarios with and without carbon price are both investigated.
4.2.1. Exclusion of carbon emission cost
Fig. 8 illustrates the total costs in all BEE and energy supply scenarios. Some important lessons can be drawn immediately by comparing the different scenarios:
1. All scenarios show that the current national BEE standard (TJ-97 equivalent efficiency requirements) is the most costly option, no matter what supply option will be selected.
2. Despite considerable progress compared with national objective, the BEE standard implemented in Tianjin (TJ 2004) is not stringent enough to allow achieving an optimal level since the present value of total costs incurred during a 20-year period can be reduced further by tightening the building code, even with a relatively high discount rate (8%).
3. Without any carbon price imposed, the optimal choice turns out to be the equivalent of current French RT-2005 building efficiency standard coupled with district coal-fired CHP, which allows for the lowest present value of the overall discounted costs (490 yuan/m2 floor space).
4. Lastly but most strikingly, we observe that adopting the best available technology (BAT), or the equivalent energy performance prescribed in the Swedish BEE standards is less costly than the current BEE regulations enforced in China and Tianjin regardless of energy supply system.
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Fig. 8. Comparison of discounted total cost in different energy supply ...