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There are very few useful work and exergy analysis studies for China, and fewer still that consider how the results inform drivers of past and future energy consumption. This is surprising: China is the world's largest energy consumer, whilst exergy analysis provides a robust thermodynamic framework for analysing the technical efficiency of energy use. In response, we develop three novel sub-analyses. First we perform a long-term whole economy time-series exergy analysis for China (1971–2010). We find a 10-fold growth in China's useful work since 1971, which is supplied by a 4-fold increase in primary energy coupled to a 2.5-fold gain in aggregate exergy conversion efficiency to useful work: from 5% to 12.5%. Second, using index decomposition we expose the key driver of efficiency growth as not 'technological leapfrog-ging' but structural change: i.e. increasing reliance on thermodynamically efficient (but very energy intensive) heavy industrial activities. Third, we extend our useful work analysis to estimate China's future primary energy demand, and find values for 2030 that are significantly above mainstream projections.
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Understanding China’s past and future energy demand: An exergy
efficiency and decomposition analysis
Paul E. Brockway
, Julia K. Steinberger, John R. Barrett, Timothy J. Foxon
Sustainability Research Institute, School of Earth and Environment, University of Leeds, LS2 9JT, UK
We complete the first time series exergy and useful work study of China (1971–2010).
Novel exergy approach to understand China’s past and future energy consumption.
China’s exergy efficiency rose from 5% to 13%, and is now above US (11%).
Decomposition finds this is due to structural change not technical leapfrogging.
Results suggests current models may underestimate China’s future energy demand.
article info
Article history:
Received 12 February 2015
Received in revised form 3 May 2015
Accepted 22 May 2015
Energy efficiency
Energy demand
Useful work
There are very few useful work and exergy analysis studies for China, and fewer still that consider how
the results inform drivers of past and future energy consumption. This is surprising: China is the world’s
largest energy consumer, whilst exergy analysis provides a robust thermodynamic framework for analys-
ing the technical efficiency of energy use. In response, we develop three novel sub-analyses. First we per-
form a long-term whole economy time-series exergy analysis for China (1971–2010). We find a 10-fold
growth in China’s useful work since 1971, which is supplied by a 4-fold increase in primary energy cou-
pled to a 2.5-fold gain in aggregate exergy conversion efficiency to useful work: from 5% to 12.5%. Second,
using index decomposition we expose the key driver of efficiency growth as not ‘technological leapfrog-
ging’ but structural change: i.e. increasing reliance on thermodynamically efficient (but very energy
intensive) heavy industrial activities. Third, we extend our useful work analysis to estimate China’s future
primary energy demand, and find values for 2030 that are significantly above mainstream projections.
Ó2015 The Authors. Published by Elsevier Ltd. This is an open accessarticle under the CC BY license (http://
1. Introduction
As the world’s economic powerhouse and largest energy
consumer [1], much effort is spent understanding China’s historical
energy consumption (e.g. [2–4]) and future energy demand [5–7].
However these studies typically examine primary or final energy
data, rather than useful work values obtained using an exergy anal-
ysis based technique. This is the research gap that this paper seeks
to address. Exergy analysis takes a broader, whole system
approach to energy analysis, giving ‘‘a measure of the thermody-
namic quality of an energy carrier’’ (p. 686, [8]), thereby enabling
a robust view of useful work consumed in provision of energy ser-
vices. Exergy analysis also has the benefit of taking into account
more aspects of the energy supply chain than traditional energy
analysis, and in a more consistent way. A flow visualisation of pri-
mary exergy to useful work is given in Fig. 1.
A key assumption in this study is that useful work is a better
‘energy parameter’ than primary energy on which to analyse end
energy use and economic activity, since – as Fig. 1 shows – it is
the last thermodynamic place where energy is measured before
it is exchanged for energy services. We are not alone in this view.
Numerous authors (e.g. [8–10]) suggest second law exergy analy-
ses can help understand national-scale energy use. For economic
insights, Percebois [11] suggested in 1979 that energy intensity
metrics (i.e. energy consumption relative to GDP) were better
undertaken at the energy output stage, since it ‘‘allows us to anal-
yse structural change in energy supply and situates our analysis at
the level of satisfied needs’’. Serrenho et al. [12] recent work on
useful work intensity supports this assertion. Meanwhile, Warr
and Ayres [13], Santos et al. [14] and Guevara et al. [15], all found
empirical evidence suggesting useful work is a better candidate as
0306-2619/Ó2015 The Authors. Published by Elsevier Ltd.
This is an open access article under the CC BY license (
Corresponding author.
E-mail address: (P.E. Brockway).
Applied Energy 155 (2015) 892–903
Contents lists available at ScienceDirect
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a factor of production (than primary energy) to explain economic
growth. This gets us to the crux of our argument: if it is useful work
and not primary energy that supplies economic needs, then we
should conduct energy and economic analyses at that level.
The few published time-series studies of useful work account-
ing have focussed largely on industrialised countries including
the US, UK and Japan (e.g. [16–18] and later all EU-15 countries
[12]. Somewhat curiously, these country-scale analyses typically
focus on economic implications and linkages, rather than
energy-based conclusions. Brockway et al. [19] set out to address
this imbalance, by undertaking a 50 year time-series analysis
(1960–2010) of the US and UK. They found the US and UK may
no longer be increasing their aggregate exergy efficiency, as
increases in process level efficiencies are offset by efficiency dilu-
tion taking place [19], following the case of Japan [17]. In short:
individual technology gains in efficiency are being overtaken by
using increasing amounts of less efficient processes, such as
air-conditioning. This raises the question: could the same be hap-
pening in China?
Numerous Extended Exergy Accounting (EEA) studies have been
published on China (e.g. [20–32]). EEA is a biophysical exergy anal-
ysis method, developed largely by Wall and Sciubba in the 1990s
(e.g. [33–35]) to examine the embedded exergy of all natural
resources inputs (e.g. energy, natural materials) and associated
outputs of the economy (e.g. food, materials, wastes). This valuable
technique helps understand societal exergy consumption. It is
complementary to the useful work accounting method applied
here, which is based on an ‘‘energy carriers for energy use’’
approach [36] introduced at a national-scale by Reistad [37] in
1975, which examines the exergy destruction of energy conversion
processes from primary exergy to end useful work. The key distinc-
tion is that EEA is akin to a mass-balance analysis (except it studies
exergy content not mass) whereas Reistad’s approach estimates
the thermodynamic work done by the energy system to deliver
energy services. It is the latter approach we require for detailed
energy system analysis – and such national-scale useful work
accounting studies for China are rare (e.g. [38]), and none to date
examine a long time-series.
To address the lack of exergy-based analyses in China which
examine time-series results through an energy demand lens, we
pose the following research question: What new insights can useful
work analysis provide for historical and future energy demand in
China? In response, we provide three novel, linked analyses. To
start, we undertake the first historical exergy efficiency and useful
work analysis for China, covering the period 1971–2010. Next, we
adopt an index decomposition analysis to identify the key drivers
of change in China’s useful work. Last, we develop a useful work
based method for projecting China’s primary energy demand to
2030, and also test implications of potential future declines in
the rate of exergy efficiency improvement.
The paper proceeds as follows. After the Introduction, Section 2
contains Methods and Data, Results and Discussions are in
Section 3, with Conclusions in Section 4.
2. Methods and data
2.1. Historical useful work analysis (1971–2010)
2.1.1. Method Summary
Reistad [37] defined exergy as ‘available energy’. As depicted
in Fig. 1, at a country-scale, primary exergy of energy carriers
(e.g. coal, oil, gas, renewables, food and feed) is transformed into
ready to use ‘final energy’ (e.g., diesel or electricity), which is
then used to provide ‘useful work’ (i.e. through heat, mechanical
drive, manual labour or electrical devices), to ultimately provide
energy services (e.g. warmth, light, cooling, sustenance).
Carnahan et al. [39] defined task-level ‘useful work’ ðU
‘‘the minimum exergy input to achieve that task work transfer’’.
For our purposes, task-level means sub-class (j) (e.g. diesel road
transport or low temperature heat) levels nesting within overall
main classes (i) of energy use (i.e. heat, muscle work, transport,
mechanical drive). Task-level exergy efficiency ð
the second law thermodynamic efficiency of the energy conver-
sion from primary exergy to end useful work, defined by
Carnahan et al. [39] as:
Primary exergy values at task-level ðE
Þare then multiplied
with their associated task-level exergy efficiencies (
) to give an
estimate for task-level useful work ðU
Þ. When summed, we derive
an overall estimate for the total national-scale useful work
Þvia Eq. (2). Finally, national exergy (second law) effi-
ciency (
) is given by Eq. (3), which – following Carnahan et al.
[39] – we adopt as a country-scale measure of energy efficiency,
and use it as a term throughout this paper for consistency. Eq.
(2) also reveals the obvious (but important, as we see later) obser-
vation that useful work changes are supplied by changes in pri-
mary exergy and/or exergy efficiency.
Fig. 1. Conceptual diagram of primary exergy to useful work.
¼Useful work;U
Primary Exergy;E
¼The minimum exergy input to achieve that task work transfer
Maximum amount of reversible work done as system reaches equlibrium ð1Þ
P.E. Brockway et al. / Applied Energy 155 (2015) 892–903 893
Our country-scale useful work accounting approach builds on
the methodology developed by numerous authors including
Reistad [37], Wall [40], Ayres and Warr [41], and more recently
Serrenho et al. [42], who introduced a consistent International
Energy Agency (IEA) based input energy mapping framework.
Brockway et al. [19] made further advances to electricity applica-
tions and mechanical drive classes, which is also used in this study
for consistency and comparability. We apply these advances to
produce a first time-series analysis of China. Fig. 2 gives an over-
view of the basic stages:
2.1.2. Input data
Primary exergy inputs, E
;are first derived. IEA energy datasets
1971–2010 (1) for fossil fuel and biomass (combustible renew-
ables) provided much of the base data. IEA primary energy values
are converted to primary exergy inputs using chemical exergy
coefficients [43]. At an aggregate level, total primary exergy is
around 5% higher than the IEA’s Total Primary Energy Supply
(TPES) values. The inputs E
are then mapped to three main classes
(heat, mechanical drive and electricity) and to task-levels where
possible (e.g. Low Temperature Heat (LTH)), following recent
approaches [19,42]. The task-levels are listed in Appendix A.In
some cases, we extend the IEA end energy use breakdown to more
granular levels (e.g. road fuel split between transport modes) by
supplementing Chinese end consumption data in three key areas:
buildings [3,44–48]; transport [49–53]; and industry [54–58].
Next, task-level exergy efficiencies ð
Þfor transport, heat, and
electricity are added. Previous US–UK values [19] are modified by
Chinese data as follows. For transport, local fuel economy data
was used for road and rail [52,53,59,60]. For calculating Carnot effi-
ciencies (for heat exergy efficiencies), for external temperatures we
used 1971–2010 China monthly air temperature data [61], whilst
indoor temperatures (for LTH efficiencies) were weighted for
China’s city/rural split and assume a 20 year lag in comfort levels
versus UK data [62]. LTH first law efficiencies are based on Warr
et al. [18], Chen et al. [30] and Edwards et al. [63]. Steel and ammo-
nia industries are adopted (as with US–UK study) as representative
of High Temperature Heat (HTH) efficiencies, by virtue of having
the two highest proportions of Chinese industrial energy use
[58]. Process (GJ/tes) efficiency data for steel [54–57,64,65] and
ammonia (taken as 75% of UK values, based on average values from
Phylipsen et al. [65]) and the IEA [66] are combined with temper-
ature data to calculate time-series exergy efficiencies. For electric-
ity application efficiencies, values of 80% of those from the US–UK
analysis were typically used, based on evidence that China’s aver-
age devices were 10–20 years behind US–UK values across indus-
try, commerce and residential sectors [3,67].
Then, we calculated primary exergy and useful work values for
a fourth main class: muscle work. For human labour, estimates fol-
low Brockway et al. approach [68]: using manual labour popula-
tion [69,70], food intake data [71,72], and Smil’s estimated 13%
conversion efficiency of food to human useful work [73]. For
draught animals, we assumed 100 million draught animals in
China in 1990 [74], and a 1% annual decline in numbers from
1971 to 2010, mirroring India [75]. For animal useful work outputs,
we assumed 400 W average power output for a 5 h working day
over 120 working days/year, based on published data [74,76,77].
Estimates of intake feed requirements were based on
Ramaswamy and Krausmann [74,78].
Last, a note on data quality. For input energy data, two system-
atic discrepancies mean our national-level datasets underestimate
actual primary energy use. First, at a national-scale, IEA-based TPES
values are 5% lower than those of Lawrence Berkeley National
Laboratory (LBNL) China Energy Databook [46]. Second, reported
aggregate primary energy consumption in China is 10% higher
from aggregated regional versus national datasets [79]. However,
these differences are expected to be systematic, and thus have lim-
ited overall effect for our trends analysis. For task-level efficiencies,
whilst the China data sources are weaker in many instances than
the previous US–UK studies [19], overall trends and comparison
to US–UK results remain valid.
2.1.3. Useful work accounting outputs
Appendix A shows the task-level outputs of useful work, pri-
mary exergy and exergy efficiency. This data serves as task-level
inputs to the Logarithmic Mean Divisia Index (LMDI) decomposi-
tion analysis, or is summed to give useful work or exergy efficien-
cies at main class level (i.e. heat, mechanical drive, electricity and
muscle work) and country-scale.
2.2. LMDI decomposition (1971–2010)
LMDI decomposition is now the mainstream Index
Decomposition Analysis (IDA) technique for analysing drivers of
changes in CO
emissions (e.g. [80,81]) and sectoral energy use
such as manufacturing and transport (e.g. [82,83]). Using the
LMDI approach, we develop a new approach to reveal the relative
contribution of energy and efficiency drivers to China’s historical
useful work (U). First, we expand Eq. (2) (U=PE
) to yield Eq.
(4), which is based on task-level useful work (U
) and primary
exergy (E
), enabling the historical results to act as the input data
for the LMDI analysis. Eqs. (5)–(9) give the four drivers of useful
work changes: Input Exergy (D
); Main class structure (D
IEA Primary Energy data
(fossil fuels and biomass)
IEA Primary energy mapping
to task-level end uses
Food and feed data
Exergy chemical equivalent
conversion values
Primary exergy mapping to
Useful Work, Eij
Local country energy data
(e.g. electricity end use)
Task level exergy
Useful Work
results, U ij
Fig. 2. Useful work analysis flowchart.
894 P.E. Brockway et al. / Applied Energy 155 (2015) 892–903
sub-class (i.e. task) level structural change (D
); and task-level
efficiency (D
). This shows how LMDI decomposition can be used
to breakdown the overall exergy efficiency changes (from the main
analysis results in Section 3.1) into three parts (D
¼exp X
ln X
! ! ð6Þ
¼exp X
ln S
! ! ð7Þ
¼exp X
ln L
! ! ð8Þ
¼exp X
ln F
! ! ð9Þ
Þ=ðln U
ln U
Þ=ðln U
ln U
! ð10Þ
E= Primary exergy input to economy
= Main class exergy input
= Task-level exergy input
= Task-level useful work output
= log mean weighting function
X= Exergy input
S= Main class share of exergy input (E
L= Task-level share of exergy input within main class (E
F= Task-level exergy efficiency(U
= change in overall exergy input (E)
= change in share of exergy inputs between main classes (E
= change in task-level shares (E
) of exergy inputs within
each main class
2.3. China energy demand scenarios 2010–2030
After conducting the historical and decomposition analyses, we
develop and trial a new useful work-based methodology to esti-
mate primary energy demand to 2030, based on projections of
GDP and extrapolations of task-level exergy efficiencies under
illustrative constant and declining exergy efficiency growth rate
scenarios. Four steps were required. The first estimates China’s
useful work requirement for 2010–2030. To do this, 1971–2010
overall useful work energy intensity (UW/GDP) – calculated from
historical GDP data [84] – is extrapolated using a best-fitting curve
to 2030. Using World Bank forecasts of GDP for 2011–2030 [85]
see also the Supplementary Information – Section S1, China’s total
useful work (to deliver that GDP) in 2030 is then estimated.
Second, total projected useful work to 2030 is allocated to
task-levels. To start, useful work proportions from main classes
are estimated based on historic trend comparison in UK, US and
China. China and US allocations are shown in Fig. 3. Then, task level
allocations are derived, also based on comparisons to previous
US-UK values, which place China as 40 years behind US–UK allo-
cations. These results at task-level are given in the Supplementary
Information – Section S2.
Third, task-level exergy efficiencies are projected to 2030 under
two illustrative scenarios which have different efficiency gains
assumptions. In Scenario 1 (constant efficiency gains), China’s
1990–2010 task-level exergy efficiency changes are extended to
2010–2030. Typically this places China’s task-level efficiencies in
2030 as those of average US-UK values in 2010. In Scenario 2
(declining efficiency gains), only half of China’s 1990–2010 effi-
ciency gains are extended to 2010–2030, with two thirds of these
reduced gains assumed to occur in 2010–2020. There is some jus-
tification for the declining gains scenario, as Brockway et al. [19]
found that efficiency gains in important task-levels (e.g. residential
electricity and LTH) slowed or reversed in 1990–2010 (versus
1970–1990). Assuming an average 20 year lag for China, this could
mean similar effects exhibited in China by 2030. More detailed effi-
ciency results at task-level are given in the Supplementary
Information – Section S3. Whilst other efficiency scenarios are pos-
sible (and indeed probable), our two selected cases are intended to
represent the possible envelope of task-level efficiencies for 2010–
2030, and are thus valid to study the effects of declining efficiency
Fourth, estimates of total primary energy demand for 2010–
2030 are made at task-level (Eq. (11)) and aggregate level (Eq.
(12)). Suffix 1 and 2 refer to Scenario 1 and 2. Finally, the chemical
exergy conversion ratios [43] are removed to reveal primary
Fig. 3. China (1971–2030) and US (1860–2010) useful work allocations.
P.E. Brockway et al. / Applied Energy 155 (2015) 892–903 895
energy (i.e. TPES) projections to 2030 under these two scenarios,
with differences suggesting impacts of declining exergy efficiency
gains on primary energy demand.
3. Results and discussion
3.1. 1971–2010. useful work accounting results
Table 1 summarises useful work, primary exergy and exergy
efficiency results for 1971–2010, with task-level results given in
Appendix A for 1971 and 2010. China’s end useful work has
increased 10-fold since 1971, with electricity applications and
HTH industrial uses growing from 30% to 53% of total useful work.
Conversely, muscle work and low temperature heat have together
declined from 40% of total useful work to 8%.
Aggregate exergy efficiency has grown almost linearly from
5.3% to 12.5%. Table 1 (together with Appendix A) suggest a key
factor is the structural shift from (low efficiency) muscle work
and low temperature heat (20 °C) to (high efficiency) HTH. Fig. 4
illustrates a second reason: the strong growth in mechanical drive
and heat class efficiencies – which make up over half of total pri-
mary exergy inputs. The question of whether this linear aggregate
efficiency trend can continue is considered via the future scenario
analysis in Section 3.3.
Fig. 4 also compares China’s aggregate efficiency growth to the
stable US (10–11%) values from the previous US-UK study [19].
China’s exergy efficiency overtakes the US by around 2004. At first,
it is tempting to see China’s overtaking of the US’s aggregate effi-
ciency as ‘technological leapfrogging’ (e.g. [86]) – i.e. rapidly adopt-
ing high-efficiency technologies without having to deal with the
legacy of past low efficiency capital stock. In fact this is not the
case, since task-level exergy efficiencies are generally lower than
the US (except mechanical drive, which is a small component of
China’s energy use). This result implies structural differences make
a significant contribution to China’s increasing efficiency: i.e. its
production-focused industrial economy uses more high tempera-
ture heat and industrial processes versus the US’s mature con-
sumer economy. The index decomposition results in Section 3.2
support this view. In turn, this implies as China’s economy also
matures and its structure shifts towards that of the US, that this
may have a diluting effect on future overall exergy efficiency, as
seen later in Section 3.3.
Table 1
Summary of useful work analysis results 1971–2010.
Useful work analysis: output category 1971 1980 1990 2000 2010
Main category end use PJ % of total PJ % of total PJ % of total PJ % of total PJ % of total
Useful work
Direct heat 1087 71 1848 71 2787 68 3901 59 7602 51
Mechanical Drive 126 8 268 10 477 12 1140 17 2633 18
Electricity end uses 154 10 343 13 684 17 1460 22 4665 31
Muscle work 157 10 151 6 148 4 137 2 127 1
Total 1524 100 2610 100 4096 100 6638 100 15027 100
Primary exergy
Direct heat 15370 54 21560 56 28271 55 31504 49 51983 43
Mechanical Drive 1090 4 1971 5 2988 6 5625 9 12720 11
Electricity end uses 1592 6 3519 9 6283 12 13951 22 42507 35
Muscle work 10661 37 11760 30 13489 26 13398 21 13159 11
Total 28713 100 38810 100 51032 100 64478 100 120,369 100
Exergy efficiency (useful work/primary exergy)
Main category end use % efficiency % efficiency % efficiency % efficiency % efficiency
Direct heat 7.1 8.6 9.9 12.4 14.6
Mechanical Drive 11.6 13.6 16.0 20.3 20.7
Electricity end uses 9.7 9.7 10.9 10.5 11.0
Muscle work 1.5 1.3 1.1 1.0 1.0
Total 5.3 6.7 8.0 10.3 12.5
Fig. 4. China’s exergy efficiency by end use 1971–2010, compared to US aggregate efficiency.
896 P.E. Brockway et al. / Applied Energy 155 (2015) 892–903
Few comparative estimates are available of aggregate Chinese
efficiencies. Chen and Chen [30] calculate a value of 20%, twice that
of our 10% value for China in 2000. The main reasons are due their
exclusion of muscle work, and higher industry efficiency (e.g. 78%
for the chemical sector). Nakicenovic [87] estimated reforming
countries (e.g. China) exergy efficiencies in 1990 to be 10%, of a
similar order to our 8% estimate for 1990.
Fig. 5 shows how China’s 10-fold useful work growth was sup-
plied by a 4-fold increase in primary energy coupled to a 2.5-fold
gain in aggregate exergy efficiency: from 5% to 12.5%. In other
words, if China’s exergy efficiency had stayed at 5%, a 10-fold gain
in primary exergy would have been required to achieve the same
useful work supply level.
Finally, to understand the overall flow of exergy to end useful
work, and the exergy losses that occur during the various conver-
sion processes, useful work-based Sankey diagrams of China are
constructed for 1971 and 2010, as shown in Appendix B. They
show the transformation of China in 40 years from a largely agri-
cultural to industrial economy. By 2010, China is dominated by
energy dense fossil fuel inputs (versus food and feed for muscle
work) and energy intensive end uses, particularly in industry,
which underpins the rise in overall exergy efficiency.
3.2. LMDI decomposition results 1971–2010
The multiplicative factors are summarised in Table 2 for the
period 1971–2010, comparing three countries: China, the UK and
US. For China, the largest contribution to useful work growth is pri-
mary exergy, confirming the result of Fig. 5 Importantly, the overall
efficiency gain factor (2.5) is now split into three parts. First, the
main class structural change (1.39) tracks the move from less effi-
cient (i.e. muscle work) to more efficient (i.e. heat) main classes.
Second, we find sub-class structural change (1.19) is above 1.00,
which means that within each main class there has also been an
efficiency ‘concentration’ effect. (In contrast note the efficiency
‘dilution’ values of 0.87–0.88 for the US and UK). This is due to
China’s transition from agricultural society to industrial powerhouse,
causing structural shifts within main classes from lower to higher
efficiency categories (e.g. LTH to HTH). Third, task-level efficiency
gains (1.48) are the largest of the three efficiency gain factors.
The value of using the LMDI approach is also highlighted by
Table 2. Firstly, it confirms and quantifies the assertion stated in
Section 3.2: that overall structural change (1.66) is at least as
important to overall efficiency gains as task-level efficiency gains
(1.48). Secondly, we can directly compare factors to other coun-
tries. In this case, we see that China has not reached the point of
efficiency ‘dilution’ that can be seen in the US and UK – where
would be below 1.00 – as found earlier by Williams et al.
[17] for Japan. China’s improvements to task-level efficiencies
(1.48) are similar to US (1.29) and UK (1.58) values, confirming that
instead of technological leapfrogging, it is overall structural change
(1.66 for China versus 0.90 for US and UK) that has been responsi-
ble for China’s rise in overall aggregate efficiency to overtake the
3.3. Future exergy efficiency: impacts on primary energy projections
3.3.1. Step 1 – Useful work projection to 2030
China’s useful work and primary energy intensities (of eco-
nomic activity) are shown in Fig. 6, based on constant price GDP.
It shows a 66% reduction in useful work intensity from 12.0
(GJ/2005$US) in 1971 to 3.9 (GJ/2005$US) in 2010, compared to
an 86% reduction in primary energy intensity (210.7 to
29.8 GJ/2005$US) the standard metric for energy intensity (e.g.
[88]) – over the same period. The greater stability of useful work
intensity suggests useful work is more closely linked to GDP than
primary energy – supporting the key assumption noted earlier.
Useful work and primary energy intensities are projected to 2030
using best-fitting trendlines as shown in Fig. 6.
The World Bank’s GDP forecast for China in 2030 [85] is
$13.5 Trillion(US2005), a 3.5-fold increase from the
$3.8 Trillion(US2005) value in 2010. Using the useful work inten-
sity projection of 2.45 (GJ/US$2005) for 2030, this gives a useful
work estimate of 33.1EJ in 2030 (just over double the 15.0EJ con-
sumed in 2010) – to deliver that level of GDP.
3.3.2. Step 2 – Allocation of task-level useful work
Fig. 7 shows the projected annual useful work growth to 2030 is
almost linearly 27–28 Mtoe/year. This is due to two effects can-
celling each other out: a slowdown in GDP growth mirroring useful
work intensity reductions. At a main class level, as China’s econ-
omy matures, a slowdown in heat’s contribution to useful work
is offset by growth in electricity and mechanical drive (mainly
transport) classes. This appears broadly consistent with other eco-
nomic forecasts for China used in energy modelling (e.g. [6]).
Table 2
Summary of LMDI decomposition factors 1971–2010 for China, US, UK.
Country U Dex Dstr Ddil Deff
Main class
China 9.76 3.96 1.39 1.19 1.48
US 1.53 1.32 1.03 0.88 1.29
UK 1.43 1.01 1.04 0.87 1.58
Country UD
Overall structural change Task-level
China 9.76 3.96 1.66 1.48
US 1.53 1.32 0.90 1.29
UK 1.43 1.01 0.90 1.58
Fig. 5. China 1971–2010 useful work analysis results vs 1971 datum.
P.E. Brockway et al. / Applied Energy 155 (2015) 892–903 897
3.3.3. Step 3 – Task-level exergy efficiencies
Next, task-level exergy efficiencies are projected based on the
linear and declining gains scenarios described earlier – see
Supplementary Information. The results at main class level are
shown in Fig. 8. In Scenario 1, stable gains in task-level exergy effi-
ciencies are combined with structural change in China in 2011–
2030 – moving towards a more service sector-based economy,
with associated decreases in higher efficiency processes (e.g. high
temperature heat) and increases in low-efficiency activities (e.g.
residential and commercial electricity), as shown earlier in Fig. 3.
This results in only a small increase in national aggregate exergy
efficiency from 12.5% to 13.0% in 2030. The green wedge in Fig. 8
illustrates the effect of this structural change, compared to a sim-
ple extrapolation of China’s 1990–2010 aggregate efficiency, which
would result in aggregate exergy efficiency of around 17% in 2030.
In Scenario 2, which includes both structural change and slowing
of task-level efficiency gains, aggregate exergy efficiency peaks at
12.8% before 2025, then reduces to 12.5% by 2030. Therefore most
of the reduction in overall efficiency is due to assumed structural
change than the difference in task-level efficiencies under the
two scenarios.
For heat and mechanical drive classes, the projected efficiency
dilution is so strong (i.e. less industrial usage and more consumer/
commercial use), their efficiencies decline by 2030 under both sce-
narios. As electricity provides an increasing share of useful work by
2030, this accelerates the slowdown (scenario 1) and decline (sce-
nario 2) in overall exergy efficiency. Mechanical drive efficiency
stagnates in this analysis under both scenarios, since it balances
task-level efficiencies that were increasing (e.g. static motors and
aviation) and decreasing (e.g. road transport – due to more
Primary Energy Intensity (GJ/US$2005)
Fig. 6. Comparison of China primary energy and useful work intensities.
Fig. 7. China – useful work projection to 2030.
Efficiency scenario differences
Structural change
Fig. 8. China – exergy efficiency scenario results.
898 P.E. Brockway et al. / Applied Energy 155 (2015) 892–903
cars/less motorcycles, and more heavy duty-trucks). However, as
the smallest of the three main classes, this effect has limited
impact on the aggregate exergy efficiency.
3.3.4. Step 4 – Primary end demand in 2030
Finally, the useful work-based primary energy estimates are cal-
culated based on the assumed efficiency scenarios. The results are
compared in Fig. 9 to five published reference (i.e. current policies)
scenarios [67,89–92] and a top-down primary energy intensity
(TPES/GDP) based estimate (derived econometrically via the
best-fit TPES/GDP projection shown earlier in Fig. 6). By 2030, our
Scenario 1 (6000 Mtoe/year) requires 900 Mtoe/year more primary
energy than the econometric estimate, whilst Scenario 2 – due to
assumed declining efficiency gains – requires an additional
300 Mtoe/year (compared to Scenario 1). The TPES/GDP derived pri-
mary energy estimate (as with the other five reference projections)
slows over time, following the assumed slow-down in GDP growth.
In contrast, our useful work derived projections show more linear
increases, as with flat overall exergy efficiencies (shown earlier in
Fig. 8), the linear projected growth in useful work required (see ear-
lier Fig. 7) is passed on to required primary energy inputs.
Our useful work-based projections are significantly higher than
the five reference cases. The three reference scenarios using a 2010
base year [89–91] produce estimates of 4300–5000 Mtoe/year in
2030, whilst the two scenarios with a 2005 base year [67,92] esti-
mate primary energy consumption as 3200 Mtoe in 2030. A key
aspect therefore appears the choice of base year, with the 2005
base year models missing China’s step up in energy consumption,
and so undercut the projections of later base year models.
Perhaps this illustrates how tricky energy forecasting is, as Smil
[93] notes: ‘‘long-range energy forecasters have missed every
important shift of the past 2 generations..[and they]..will continue
to be wrong’’.
Nevertheless, the fact remains the traditional energy models
give lower estimates of primary energy than our simple useful
work-based approach – so it’s worth reflecting on this. Most
importantly, we base our projections on a different energy inten-
sity metric versus mainstream models – ours is based on useful
work (U/GDP), as this measures the energy level delivered to eco-
nomic activities, rather than on primary energy (TPES/GDP) enter-
ing the economy. Moreover, our TPES/GDP based projection is 20%
below our U/GDP based projections – showing that this distinction
is an important one. The GDP projections that we use are consis-
tent with other models (e.g. [6]). Our methodology is also
top-down: it starts from an aggregate demand estimation, and
then builds up its constituent elements from task-share trends.
Other energy models tend to be bottom-up, using demand and
technology trends of various sectors. We attach more detailed sce-
nario data in the Supplementary Information.
Whilst we believe the useful work based approach to primary
energy forecasting is justified by the observed links between
aggregate economic activity and useful work, significant caveats
exist around the accuracy of the underlying data to our energy pro-
jection conclusions. For the useful work calculations for 1971–
2010, though the primary exergy data is relatively robust (relying
mainly on IEA energy balance data), the task-level efficiencies have
greater uncertainty, being based on often partial data. In turn, pro-
jecting task-level useful work allocations and exergy efficiencies to
2030 amplifies any data inaccuracies. However the driving ratio-
nale of the paper was to develop a new technique based on useful
work. The result highlights the possible importance of this method
and thus mandate for further study.
4. Conclusions
To address the lack of time-series exergy analyses for China
which examine energy demand drivers and implications, we set
the following research question: What new insights can useful work
analysis provide for historical and future energy demand in China?
First, our historical analysis found China’s exergy efficiency grew
linearly from 5.3% (1971) to an impressive 12.5% (2010), placing
it between the US (11%) and the UK (15%). In addition, a striking
10-fold rise in China’s useful work occurred from 1971 to 2010,
supplied by a 4-fold increase in primary exergy and a 2.5-fold
increase in exergy efficiency. Second, using LMDI decomposition
we found efficiency growth was split evenly between task-level
efficiency gains and structural change (e.g. moving from muscle
work to mechanical drive). Third, a new useful work-based energy
forecasting technique is developed and trialled, which – based on
two illustrative exergy efficiency scenarios – projects China’s
2030 primary energy demand in the range of 6000–6300 Mtoe, sig-
nificantly higher than the 4500–5200 Mtoe estimates from pub-
lished sources using traditional energy models which use the
same 2010 baseline year.
The results allow several key insights. Firstly, if China’s exergy
efficiency had stayed at 5%, a 10-fold (rather than 4-fold) gain in pri-
mary exergy would have been required to achieve the same useful
work supply level. Through the mechanism of the macro-economic
rebound effect, however, as Ayres et al. [94] and Schipper and
Grubb [95] established, lower efficiency gains may in fact translate
to lower economic growth, and hence lower required useful work.
Second, the application of LMDI decomposition to useful work
results provided robust insights: revealing China’s efficiency rise
above the US was not due to technological leapfrogging, but greater
use of energy intensive (yet more exergy efficient) industrial pro-
cesses. Third, in common with the US and UK, China may approach
an asymptotic exergy efficiency maximum by 2030, as its economy
matures and efficiency dilution starts. Such dilution is already
Fig. 9. China – primary energy (TPES) forecasts to 2030.
P.E. Brockway et al. / Applied Energy 155 (2015) 892–903 899
forecast: the modal shift to cars [67] will reduce mechanical drive
exergy efficiency; a rapid increase in residential electricity [3];
and a peaking in the share of HTH allied to a shift to greater residen-
tial LTH. Fourth, our extension of useful work based technique pro-
jects higher primary energy demand in China by 2030 versus
traditional bottom-up energy model estimates (i.e. based on pri-
mary or final energy). Further studies investigating the possible
reasons (e.g. differences in assumed future energy efficiency sav-
ings, structural consumption, energy rebound and efficiency dilu-
tion) would therefore be beneficial.
Overall, the useful work method appears a valuable technique to
give new insights into Chinese energy consumption and efficiency –
past, present and future. Given the implications to future energy
demand and associated policies, further research is encouraged.
First, work to improve the consistency of the useful work method
would be of benefit – such as the treatment of renewables,
non-energy use, active/passive system efficiencies, or extending the
analysis boundary to include energy services, as others suggest
[38,87,96]. Second, contrast the construction of traditional (primary
and final energy) versus useful work energy models, to uncover the
reasons for energy projection differences. Third, undertake further
economic analysis to test the key assumption underpinning this
work: that useful work is a more suitable parameter for energy and
economic analysis than primary energy. Lastly, policy implications
could be explored – such as how to meet higher (than expected) pri-
mary energy demand, or how to amend micro-efficiency policies to
capture energy savings before rebound occurs.
We gratefully acknowledge the support of Engineering and
Physical Sciences Research Council (EPSRC) and Arup for contribut-
ing to the PhD CASE (Collaborative Award in Science and
Engineering) scholarship of the first author. The support of the
Economic and Social Research Council (ESRC) is also gratefully
acknowledged. The work contributes to the programme of the
ESRC Centre for Climate Change Economics and Policy. Also, we
thank João de Santos and Tiago Domingos of Instituto Superior
Técnico, Lisbon, for sharing their unpublished work. We would like
to thank the two anonymous reviewers and the editor of Applied
Energy for their useful suggestions and valuable comments.
Appendix A. Useful work accounting outputs: China – 1971,
(see Table A1)
Table A1
Useful work accounting outputs: China – 1971, 2010.
Main class, iTask level, j1971 2010
PJ PJ (%) PJ PJ (%)
Heat LTH (Low Temperature Heating 20 °C) 435 10,103 4.3 973 20,281 4.8
MTH1 (Medium Temperature Heating 100 °C) 30 247 12.1 592 4428 13.4
MTH2 (Medium Temperature Heating 200 °C) 301 2657 11.3 1913 10,506 18.2
HTH (High Temperature Heating 600 °C) 283 2362 12.0 3963 16,695 23.7
Sub total 1049 15,370 6.8 7441 51,910 14.3
Mechanical drive – Gas/diesel oil (assume diesel road
20 114 17.3 821 3728 22.0
Mechanical drive – Domestic Aviation fuel, jet fuel 0 0 n/a 158 642 24.6
Mechanical drive – Gasoline fuel (Petrol road vehicles 42 242 17.3 691 3920 17.6
Mechanical drive – Diesel/gas oil fuel (Boat engines) 2 17 13.0 188 915 20.5
Mechanical drive – Industry static motors (diesel
28 118 23.5 522 1934 27.0
Mechanical drive – Gas/diesel fuel (diesel trains) 1 8 13.0 64 310 20.5
Mechanical drive – Gas/diesel fuel (tractors) 26 255 10.2 88 799 11.0
Mechanical Drive – bio-diesel/bio-gasoline (road
0 0 n/a 16 80 n/a
Mechanical drive – bio-diesel/bio-gasoline (road
0 0 n/a 0 0 n/a
Mechanical drive – Gas/diesel oil (assume diesel cars) 0 1 20.4 85 385 22.0
Mechanical drive – Gas fired engines (for pipeline
0 0 n/a 2 7 n/a
Mechanical drive – Coal (steam powered trains) 7 333 2.2 0 0 n/a
Mechanical drive – Coal (steam powered boats) 0 0 n/a 0 0 n/a
Mechanical drive sub-total 126 1090 11.6 2633 12,720 20.7
Electricity Lighting 1 84 0.8 46 2836 1.6
Domestic/commercial – Space heating 0 31 1.3 57 3303 1.7
Domestic – Hot water/cooking 1 21 3.0 47 1272 3.7
Industry – HTH process heating 16 199 7.9 443 4537 9.8
Electrolytic end use – Industry 11 153 7.5 370 3490 10.6
Communications/electric devices 0 0 0.1 1 267 0.3
Refrigeration/air conditioning 4 307 1.4 144 8221 1.7
Domestic – Wet/dry motor driven appliances 0 0 10.0 17 138 12.6
Other mechanical drive motors 123 797 15.4 3537 18,442 19.2
Electricity – Sub-total 156 1592 9.8 4662 42507 11.0
Muscle work Human 26 5432 0.5 38 9626 0.5
Draught animals 131 5229 2.5 88 3533 2.5
Muscle work – Sub-total 157 10,661 1.5 127 13,159 1.0
Total Grand total 1488 28,713 5.2 14,863 120,296 12.4
900 P.E. Brockway et al. / Applied Energy 155 (2015) 892–903
Fig. B1. China E-Sankey Diagram (1971).
Fig. B2. China E-Sankey Diagram (2010).
Appendix B. Primary exergy to useful work E-Sankey flowmaps: China – 1971 and 2010
(see Figs. B1 and B2)
P.E. Brockway et al. / Applied Energy 155 (2015) 892–903 901
Appendix C. Supplementary material
Supplementary data associated with this article can be found, in
the online version, at
Appendix D. Data Statement. Supplementary material
A complete results file, produced following the methodology
and sources described in this paper, has been deposited at the
University of Leeds Data Repository at
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P.E. Brockway et al. / Applied Energy 155 (2015) 892–903 903
... This emerging picture of the role of useful exergy and efficiency on economic growth and energy consumption (and CO 2 emissions) is illuminating. However, current understanding is based on analyses of single countries [17,[22][23][24][25]27,28] or a small number of countries (between 2 and 15 countries) [18,26] over short timescales (40-50 years) [18,24,26,28] with little-to-no electricity end-use detail [25,27]. A few studies [17,22,23] have longer timescales with more detail on electricity consumption but focus on single countries (Portugal and US). ...
... This emerging picture of the role of useful exergy and efficiency on economic growth and energy consumption (and CO 2 emissions) is illuminating. However, current understanding is based on analyses of single countries [17,[22][23][24][25]27,28] or a small number of countries (between 2 and 15 countries) [18,26] over short timescales (40-50 years) [18,24,26,28] with little-to-no electricity end-use detail [25,27]. A few studies [17,22,23] have longer timescales with more detail on electricity consumption but focus on single countries (Portugal and US). ...
... Our world results do not show a decrease in primary-to-final exergy efficiency as found in the the long-term study for Japan [25], because hydro was not as significant at the world level as in Japan. Regarding primary-to-useful exergy efficiency, we estimate an increase of 1% for 1960-2010, in line with the result for China [28], USA, and UK [26]. ...
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In the coming renewables-based energy transition, global electricity consumption is expected to double by 2050, entailing widespread end-use electrification, with significant impacts on energy efficiency. We develop a long-run, worldwide societal exergy analysis focused on electricity. Our 1900–2017 electricity world database contains the energy carriers used in electricity production, final end-uses, and efficiencies. We find world primary-to-final exergy (i.e. conversion) efficiency increased rapidly from 1900 (6%) to 1980 (39%), slowing to 43% in 2017 as power station generation technology matured. Next, despite technological evolution, final-to-useful end-use efficiency was surprisingly constant (∼48%), due to “efficiency dilution”, wherein individual end-use efficiency gains are offset by increasing uptake of less efficient end uses. Future electricity efficiency therefore depends on the shares of high efficiency (e.g. electrified transport) and low efficiency (e.g. cooling and low temperature heating) end uses. Our results reveal past conversion efficiency increases (carbon intensity of electricity production reduced from 5.23 kgCO2/kWh in 1900 to 0.49 kgCO2/kWh in 2017) did little to decrease global electricity-based CO2 emissions, which rose 380-fold. The historical slow-pace of transition in generation mix and the need to electrify end-uses suggest that strong incentives are needed to meet climate goals.
... This includes exergy analysis for countries and comparing system performance based on exergy and energy. Losses in exergy could be considerably reduced in Brazil [63], Japan [95], Canada [61], Norway [23], the Netherlands [54], the UK [45], China [11], Portugal [50], and Italy [64]. Gong and Wall [26] conclude that the final useful efficiencies for most countries were about 20% when taking an exergetic perspective. ...
... An exergy approach was introduced in 1975 to analyze the USA [57]. Several other countries have been analyzed using a modified version of this approach since then [18,96,61,63,98,65,7,30,83,11,12]. ...
This paper proposes a step-by-step, replicable methodology for analyzing the exergy characteristics of a country’s energy system. It introduces a set of indicators comparable to those commonly used to describe national energy systems: (1) exergy intensity (2) exergy destruction per capita, (3) exergy destruction per gross domestic product (GDP), (4) exergy efficiency, and (5) exergetic cost. The energy efficiency of the energy sector in Mexico was roughly 20% lower than energy efficiency, with substantially less improvement over the 15 years from 2013 to 2018. This difference arises from a strong dependency on fossil fuels and associated exergy destruction, which is not immediately apparent when taking only an energy perspective. The economic value of exergy destruction could represent 2.9 % of GDP in Mexico. A decreasing trend in the final exergy consumption is not necessarily reflected in lower exergy destruction. Those indicators provide information about the Jevons’ paradox. And it points to substantial room for efficiency improvements in the energy sector, with important implications for greenhouse gas emissions. Applying the exergy perspective will allow policymakers to understand better opportunities to unlock new efficiencies and improve the sustainability of Mexico’s energy system and those of other countries.
... Intensive resource consumption is conducive to rapid economic development and wealth accumulation in a developing society. However, high dependence on natural resources and extensive development modes have caused progressively severe ecological environmental issues, especially in China (Shao et al. 2013;Brockway et al. 2015;Liu et al. 2020;Meng et al. 2022). To fulfill the established sustainable development goals, the transformation of development modes should pay more attention to the carrying capacity of supporting ecosystems and avoid overdrawing on vital production factors (Chen et al. 2014;Zhang et al. 2018). ...
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China has made huge efforts to increase the efficiency of its resources and change its resource-intensive economic trajectory. A question which should be raised is whether the impacts of such shifts can be measured. Exergy analysis provides a unified method of ecological diagnosis of resource allocation and metabolism in social systems from a biophysical perspective. This paper explores the resource utilization pattern within Chinese society by employing an exergy-based accounting method. Nationally total resource consumption amounted to 153.7 EJ in 2017, and non-biological resources reached 137.1 EJ. China’s resource self-sufficiency rate was revealed as 79.1%. After China experienced a transition period with a medium–high economic growth rate, the total net resource input into Chinese society marked an increase of around 1% from 2012 to 2017. The per capita resource consumption dropped from 112.0 GJ in 2012 to 110.6 GJ in 2017. The proportion of resource exergy consumption in the tertiary sector was upregulated from 10.0% in 2012 to 17.6% in 2017. To be specific, the exergy conversion efficiency of the domestic sector rose from 1.3% in 2012 to 20.6% in 2017. The results confirm that the resource exergy utilization structures and the conversion efficiencies of the main social sectors in China’s economic transition period were significantly optimized towards a more sustainable future. A reasonable analysis of the resource exergy utilization pattern provides a solid reference for assessing the comprehensive effect of the changed development speed, industrial structure, and driving force of a developing society.
... Studies that adopt more restricted systems boundaries, either leaving out upstream resource processing/conversion or conversely end-use and service provision, show typical exergetic efficiencies between 15% (city of Geneva (Grubler et al. 2012a)) to below 25% (Japan, Italy, and Brazil, albeit with incomplete systems coverage that miss important conversion losses (Nakićenović et al. 1996b)). These findings are confirmed by more recent exergy efficiency studies that also include longitudinal time trend analysis Brockway et al. 2014;Serrenho et al. 2014;Brockway et al. 2015;Guevara et al. 2016). Figure 5.10 illustrates how energy demand reductions can be realised by improving the resource efficiency cascades shown in Figure 5.9. ...
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Chapter 5 (Demand, services and social aspects of mitigation), explores how mitigation interacts with meeting human needs and access to services. It explores, inter alia: sustainable production and consumption; patterns of development and indicators of wellbeing; the role of culture, social norms, practices and behaviour changes; the sharing economy and circular economy; and policies facilitating behavioural and lifestyle change. This chapter is part of the Working Group III contribution to the Sixth Assessment Report of the Intergovernmental Panel on Climate Change (IPCC). Electronic copies of this chapter are available from the IPCC website; and
... This study reveals complex energy flows through energy conversion chains and provides a more consistent basis for energy efficiency research. In accordance with this energy system division, Brockway et al [38] extended the Kaya identity to include technical efficiency factors from primary energy to useful energy to understand China's past and future energy demand. Chong et al [39][40][41] The layout of the present paper is organized as follows: Section 2 describes the methods and data used in this work, focusing on the establishment of the extended Kaya identity framework. ...
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Improving energy efficiency is one of the most reliable ways toward carbon neutrality. Most previous studies have focused on how to reduce energy intensity; however, it is not enough to provide an overview of how many carbon emissions can be reduced by technical efficiency improvements underlying energy systems. To fill this gap, this study extended the common Kaya identity to systematically evaluate the carbon reduction potential from technical efficiency improvements of various technical conversion components within the energy system at a granular level. The extended Kaya identity includes technical efficiency factors of electricity efficiency, conversion efficiency, and passive efficiency. It provides a comprehensive framework to evaluate current performance, historical contributions, and future potential of technical efficiency improvements. The case of China reveals that: Currently, only around 5% of energy sources were delivered to final services. By improving technical efficiency to high levels, 59% carbon reduction can be achieved during the future energy transition, even when the economy is still growing. In the past, electricity efficiency and conversion efficiency have significantly reduced carbon emissions. Future policymakers should pay more attention to passive systems to provide more final services, such as improved room insulation, streamlined vehicle designs, and smart energy management.
Along with the growing demand and improving diet, the agricultural sector faces challenges in balancing resource consumption, environmental impacts and yields. This study presents an extended exergy accounting to capture the changing characteristics of the usefulness of resources in the agricultural sector of Hebei Province during 2000–2018 from thermodynamics perspective. The accounting includes exergy fluxes of energy, materials, environmental remediation, labor, capital and yields quantified by joules. The agricultural sector of Hebei Province comprising the cropping, forestry, stockbreeding and fishery sub industries, has experienced transformation into a modern pattern. The results showed that (1) the extended exergy in the agricultural sector of Hebei Province exhibited a declining trend; the natural resource exergy, particularly energy exergy, dominated the investments in the sector. (2) The capital exergy, labor exergy and environmental remediation exergy all decreased; the capital exergy and labor exergy decreased more than the environmental remediation exergy. The shares of the labor exergy from the services of agriculture declined, while those of the labor exergy from forestry and stockbreeding notably increased. (3) Since the cropping accounts for a large part of the yields, the large quantity of crop residues should be considered seriously. The potential of the other three sub industries was very high. The comparison between the agricultural sector in Hebei Province and that in China as a whole involving exergy indicators showed that Hebei Province was more modernized and had achieved great progresses. Extended exergy accounting captures the agro ecological economic system to help identify resource depletion and environmental costs in other areas or industries from a sustainable development perspective.
Rapid expansion, relative shortage resources supply and environmental impact threat the sustainable development of the smelting and pressing of metals sector. Fluxes of energy, materials, environmental remediation expenses, labor, and capital were quantified by Joules based on the second-law thermodynamics during years 1992–2015. The accounting method that quantifies the component of the extended exergy fluxes and the proportion in the total inputs was used to analyze this energy-intensive industry. Net per-capita exergy resource input and labor production efficiency are described the conversion of natural resource exergy to economic output and labor efficiency. The results showed the following: (1) the smelting and pressing of metals sector expands rapidly; the ferrous metals industry accounts the large part of the overall metals industry and the nonferrous metals industry grows faster than the ferrous metals industry. Natural resource exergy, especially energy exergy, dominates the investments of the metals industry. (2) Capital exergy and labor exergy decrease in the smelting and pressing of metals industry, while they increase in the nonferrous metals industry and decrease in the ferrous metals industry. Environmental exergy declines in both the nonferrous metals and ferrous metals industries. (3) The comparison of the nonferrous metals and ferrous metals industries with China as a whole, conducted by applying the two indicators for efficiency, shows that the two industries are exceeding the whole country in efficiency and have made great progress. In addition, the extended exergy analysis of smelting and pressing of metals industry is helpful in the identification of resource consumption and environmental cost in sustainable development view.
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This thesis is directed towards the issue of the long-term demand and supply of biomass for food, energy and materials. In the coming decades, the global requirements for biomass for such services are likely to increase substantially. Therefore, improved knowledge of options for mitigating the long-term production requirements and the associated effects on the Earth system is essential. The thesis gives a thorough survey of the current flows of biomass in the food system. This survey was carried out by means of a physical model which was developed as part of the work. For eight world regions, the model is used to calculate the necessary production of crops and other phytomass from a prescribed end-use of food, efficiency in food production and processing, as well as use of by-products and residues. The model includes all major categories of phytomass used in the food system, depicts all flows and processes on a mass and energy balance basis, and contains detailed descriptions of the production and use of all major by-products and residues generated within the system. The global appropriation of terrestrial phytomass production induced by the food system was estimated to some 13 Pg dry matter per year in 1992-94. Of this phytomass, about 0.97 Pg, or 7.5 percent, ended up as food commodities eaten. Animal food systems accounted for roughly two-thirds of the total appropriation of phytomass, whereas their contribution to the human diet was about one-tenth. Use of by-products and residues as feed, and for other purposes within the food system, was estimated to about 1.8 Pg dry matter, or 14 percent of the total phytomass appropriation. The results also show large differences in efficiency for animal food systems, between regions as well as between separate commodities. The feed conversion efficiencies of cattle meat systems were estimated to about 2 percent in industrial regions, and around 0.5 percent in most non-industrial regions (on gross energy basis). For pig and poultry systems, feed conversion efficiencies were roughly a factor of ten higher. The differences suggest that there is a substantial scope for mitigating the long-term production demand for crops and other phytomass by increases in efficiency and changes in dietary preferences.
In this paper, the global visual servoing micropositioning control method is studied and the imaging model is derived based on the G type stereo light microscope (SLM). The model contains no depth information and the left and right image information is used to obtain the image Jacobian matrix. Considering the dynamic characteristics of microrobot, we design an image-based controller, and then the stereo microscopic visual servoing system is transformed into a Hamiltonian system. It will simplify the stability analysis. The experimental and simulation results based on the four degree-of-freedom (DOF) microrobot system demonstrate the validity of the theory in this paper.
Aims: The industrial sector dominates the China's total energy consumption, accounting for about 70% of energy use in 2010. Hence, this study aims to investigate the development path of China's industrial sector which will greatly affect future energy demand and dynamics of not only China, but the entire world. Scope: This study analyzes energy use and the economic structure of the Chinese manufacturing sector. The retrospective (1995-2010) and prospective (2010-2020) decomposition analyses are conducted for manufacturing sectors in order to show how different factors (production growth, structural change, and energy intensity change) influenced industrial energy use trends in China over the last 15 years and how they will do so up to 2020. Conclusions: The forward looking (prospective) decomposition analyses are conducted for three different scenarios. The scenario analysis indicates that if China wants to realize structural change in the manufacturing sector by shifting from energy-intensive and polluting industries to less energy-intensive industries, the value added average annual growth rates (AAGRs) to 2015 and 2020 should be more in line with those shown in scenario 3. The assumed value added AAGRs for scenario 3 are relatively realistic and are informed by possible growth that is foreseen for each subsector. Published by Elsevier Ltd.
During this study a methodology was developed to project growth trends of the motor vehicle population and associated oil demand and carbon dioxide (CO2) emissions in China through 2050. In particular, the numbers of highway vehicles, motorcycles, and rural vehicles were projected under three scenarios of vehicle growth by following different patterns of motor vehicle growth in Europe and Asia. Projections showed that by 2030 China could have more highway vehicles than the United States has today. Three scenarios of vehicle fuel economy were also developed on the basis of current and future policy efforts to reduce vehicle fuel consumption in China and in developed countries. With the vehicle population projections and potential vehicle fuel economy data, it was projected that in 2050 China's on-road vehicles could consume approximately 614 million to 1,016 million metric tons of oil (or 12.4 million to 20.6 million barrels per day) and emit 1.9 billion to 3.2 billion metric tons (or 2.1 billion to 3.5 billion tons) of CO2 each year. Although these projections by no means imply what will happen in the Chinese transportation sector by 2050, they do demonstrate that an uncontained growth in motor vehicles and only incremental efforts to improve fuel economy will certainly result in severe consequences for oil use and CO2 emissions in China.
In order to better understand sectoral greenhouse gas (GHG) emissions in China, this study utilized a logarithmic mean Divisia index (LMDI) decomposition analysis to study emission changes from a sectoral perspective. Based on the decomposition results, recently implemented policies and measures for emissions mitigation in China were evaluated. The results show that for the economic sectors, economic growth was the dominant factor in increasing emissions from 1996 to 2011, whereas the decline in energy intensity was primarily responsible for the emission decrease. As a result of the expansion of industrial development, economic structure change also contributed to growth in emissions. For the residential sector, increased emissions were primarily driven by an increase in per-capita energy use, which is partially confirmed by population migration. For all sectors, the shift in energy mix and variation in emission coefficient only contributed marginally to the emissions changes. The decomposition results imply that energy efficiency policy in China has been successful during the past decade, i.e., Top 1000 Priorities, Ten-Key Projects programs, the establishment of fuel consumption limits and vehicle emission standards, and encouragement of efficient appliances. Moreover, the results also indicate that readjusting economic structure and promoting clean and renewable energy is urgently required in order to further mitigate emissions in China.