The Direct and Indirect Rebound Effects for Residential Heating in Switzerland
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University of Neuchatel<br />
Institute of Economic Research<br />
IRENE, Work<strong>in</strong>g paper 16-11<br />
<strong>The</strong> <strong>Direct</strong> <strong>and</strong> <strong>Indirect</strong> <strong>Rebound</strong> <strong>Effects</strong> <strong>for</strong><br />
<strong>Residential</strong> <strong>Heat<strong>in</strong>g</strong> <strong>in</strong> Switzerl<strong>and</strong><br />
Cécile Hediger* Mehdi Farsi** Sylva<strong>in</strong> Weber***<br />
* University of Neuchâtel, Institute of Economic Research, Rue Abram-Louis<br />
Breguet 2, 2000 Neuchtel, Switzerl<strong>and</strong>. Contact: cecile.hediger@un<strong>in</strong>e.ch.<br />
* University of Neuchâtel, Institute of Economic Research, Rue Abram-Louis<br />
Breguet 2, 2000 Neuchtel, Switzerl<strong>and</strong>. Contact: mehdi.farsi@un<strong>in</strong>e.ch<br />
* University of Neuchâtel, Institute of Economic Research, Rue Abram-Louis<br />
Breguet 2, 2000 Neuchtel, Switzerl<strong>and</strong>. Contact: sylva<strong>in</strong>.weber@un<strong>in</strong>e.ch.
<strong>The</strong> <strong>Direct</strong> <strong>and</strong> <strong>Indirect</strong> <strong>Rebound</strong> <strong>Effects</strong> <strong>for</strong><br />
<strong>Residential</strong> <strong>Heat<strong>in</strong>g</strong> <strong>in</strong> Switzerl<strong>and</strong> ∗<br />
Work<strong>in</strong>g paper<br />
Cécile Hediger, Mehdi Farsi, Sylva<strong>in</strong> Weber †<br />
This version: October 7, 2016<br />
Abstract<br />
Improvements <strong>in</strong> energy efficiency are seen as a key tool to decrease<br />
energy consumption, yet less is known about the reaction of household<br />
to such improvements. <strong>The</strong>y could adapt (<strong>in</strong>crease) their dem<strong>and</strong> because<br />
the relative price of the energy service has dim<strong>in</strong>ished thanks<br />
to the efficiency ga<strong>in</strong>s. Focus<strong>in</strong>g on the residential heat<strong>in</strong>g sector, we<br />
study how the households react to a ga<strong>in</strong> <strong>in</strong> efficiency of their heat<strong>in</strong>g<br />
system. An <strong>in</strong>creased dem<strong>and</strong> <strong>for</strong> the heat<strong>in</strong>g service is the direct rebound<br />
effect, while the <strong>in</strong>direct rebound effect is the <strong>in</strong>come effect on<br />
the consumption of all other goods. Both effects take back some of the<br />
energy sav<strong>in</strong>gs <strong>in</strong>itially expected. To estimate these rebound effects,<br />
we use a specific survey conta<strong>in</strong><strong>in</strong>g <strong>in</strong>novative choice experiments. We<br />
f<strong>in</strong>d that 10 to 15% of the expected energy sav<strong>in</strong>gs are not realised <strong>in</strong><br />
the space heat<strong>in</strong>g sector due to the direct rebound effect. Includ<strong>in</strong>g<br />
the <strong>in</strong>direct rebound effects, it is one third of the potential sav<strong>in</strong>gs<br />
which are lost. We also highlight the heterogeneity among people:<br />
some do not rebound at all, while others display a large rebound. We<br />
analyse this heterogeneity us<strong>in</strong>g socio-economic characteristics, f<strong>in</strong>d<strong>in</strong>g<br />
that people with a low <strong>in</strong>come, less educated, less environmentally<br />
friendly, <strong>and</strong> less satisfied of their heat<strong>in</strong>g com<strong>for</strong>t have the largest<br />
direct rebound effect.<br />
JEL Classification: D12, Q41, Q47, R22.<br />
Keywords: <strong>Rebound</strong> <strong>Effects</strong>, Energy Efficiency, <strong>Residential</strong> <strong>Heat<strong>in</strong>g</strong><br />
∗ This research was f<strong>in</strong>ancially supported by the Swiss National Science Foundation<br />
(SNSF), grant No 100018-144310.<br />
† University of Neuchâtel. Correspond<strong>in</strong>g author: cecile.hediger@un<strong>in</strong>e.ch.<br />
1
1 Introduction<br />
<strong>The</strong> easiest way to save energy is not to waste it. Improv<strong>in</strong>g energy efficiency<br />
is thus considered a key tool to reduce energy consumption while<br />
keep<strong>in</strong>g the same level of com<strong>for</strong>t. Energy efficiency is <strong>in</strong>deed seen as the<br />
“Fifth Fuel” or “Invisible Fuel” (<strong>The</strong> Economist, 2015) of the energy transition.<br />
In Switzerl<strong>and</strong>, like <strong>in</strong> many other <strong>in</strong>dustrialized countries, room <strong>for</strong><br />
improvements <strong>in</strong> energy efficiency is still considerable, especially <strong>in</strong> the area<br />
of build<strong>in</strong>gs <strong>and</strong> heat<strong>in</strong>g systems. Accord<strong>in</strong>g to the Swiss Federal Office of<br />
Energy, 30% of Switzerl<strong>and</strong>’s primary energy consumption is attributable to<br />
heat<strong>in</strong>g, air-condition<strong>in</strong>g <strong>and</strong> hot water <strong>in</strong> the build<strong>in</strong>gs, with much of the<br />
energy be<strong>in</strong>g wasted. Promot<strong>in</strong>g energy efficiency is the first pillar of the<br />
energy strategy 2050 aim<strong>in</strong>g to phase out nuclear power, com<strong>in</strong>g be<strong>for</strong>e the<br />
promotion of renewable. In terms of efficiency, four sectors are targeted, with<br />
build<strong>in</strong>gs <strong>in</strong> the first position, <strong>and</strong> then mobility, <strong>in</strong>dustry, <strong>and</strong> appliances.<br />
Yet, sett<strong>in</strong>g ambitious efficiency st<strong>and</strong>ards might not be sufficient to achieve<br />
the new targets of energy consumption, because people will react <strong>and</strong> adjust<br />
to such policies. <strong>The</strong>se reactions must be acknowledged <strong>in</strong> order to design<br />
effective policies. Follow<strong>in</strong>g efficiency improvements, consumers could react<br />
by consum<strong>in</strong>g more goods <strong>and</strong> services, with the risk of offsett<strong>in</strong>g completely<br />
the <strong>in</strong>itial ga<strong>in</strong>s <strong>in</strong> energy consumption. For example, suppose the heat<strong>in</strong>g<br />
system of your house has just been renovated <strong>and</strong> is now more efficient. It<br />
means that it is now cheaper to heat your house. Because of that, you could<br />
decide to modify your heat<strong>in</strong>g habits, <strong>for</strong> <strong>in</strong>stance set the temperature by 1<br />
or 2 degrees higher, or start heat<strong>in</strong>g earlier <strong>in</strong> the season, air more often,<br />
etc. This mechanism is known as the “rebound effect”, or more precisely the<br />
direct rebound effect. In the literature, the direct rebound effect is commonly<br />
def<strong>in</strong>ed as “an <strong>in</strong>creased consumption of energy services [e.g., heat<strong>in</strong>g] follow<strong>in</strong>g<br />
an improvement <strong>in</strong> the technical efficiency of deliver<strong>in</strong>g those services”<br />
(Sorrell <strong>and</strong> Dimitropoulos, 2008).<br />
An <strong>in</strong>direct rebound effect might also arise because products <strong>and</strong>/or services<br />
will be purchased with the sav<strong>in</strong>gs made on heat<strong>in</strong>g. <strong>The</strong> use of the term<br />
2
<strong>in</strong>direct rebound is <strong>in</strong>consistent <strong>in</strong> the literature, but it most commonly describes<br />
the <strong>in</strong>come effect on the consumption of all other goods (Chan <strong>and</strong><br />
Gill<strong>in</strong>gham, 2015). As any product <strong>and</strong> service requires energy to be created<br />
<strong>and</strong> used, overall energy consumption will decrease by less than the amount<br />
predicted after the renovation of an heat<strong>in</strong>g system, even <strong>in</strong> the absence<br />
of any direct rebound effect. In the worst case, if the products or services<br />
purchased with the sav<strong>in</strong>gs made on heat<strong>in</strong>g are very energy <strong>in</strong>tensive (<strong>for</strong> <strong>in</strong>stance<br />
travell<strong>in</strong>g by plane), overall energy consumption could even <strong>in</strong>crease.<br />
<strong>The</strong> latter situation is known as backfire.<br />
In this paper, we <strong>in</strong>vestigate the direct <strong>and</strong> <strong>in</strong>direct rebound effects <strong>for</strong> residential<br />
heat<strong>in</strong>g <strong>in</strong> Switzerl<strong>and</strong>. As efficiency is seen as a key tool to decrease<br />
energy consumption <strong>and</strong> <strong>in</strong> turn CO 2 emissions, a reliable estimation of<br />
these rebound effects is highly valuable <strong>for</strong> policy makers <strong>in</strong> charge of the<br />
energy transition. Besides, we also analyse <strong>in</strong>dividual heterogeneity <strong>and</strong> determ<strong>in</strong>e<br />
who rebounds the most. In the literature, hypotheses suggest that<br />
people less satisfied with their heat<strong>in</strong>g com<strong>for</strong>t will rebound more. Yet, such<br />
hypotheses are never tested due to the lack of data, except <strong>for</strong> the impact<br />
of <strong>in</strong>come (Chitnis et al., 2014) <strong>and</strong> ownership (Madlener <strong>and</strong> Hauertmann,<br />
2011).<br />
Our data come from a survey that we created <strong>for</strong> this purpose. <strong>The</strong> 3,500<br />
respondents answered a choice experiment <strong>in</strong> which improvements <strong>in</strong> the efficiency<br />
of their heat<strong>in</strong>g system were simulated. To our knowledge, this k<strong>in</strong>d of<br />
experiment has never been conducted to estimate both direct <strong>and</strong> <strong>in</strong>direct rebound<br />
effects. Furthermore, measur<strong>in</strong>g rebound effects <strong>for</strong> residential heat<strong>in</strong>g<br />
has received few attention, with only a h<strong>and</strong>ful studies <strong>in</strong> Europe (Haas <strong>and</strong><br />
Biermayr, 2000; Madlener <strong>and</strong> Hauertmann, 2011; Druckman et al., 2011;<br />
Chitnis et al., 2013). However, results show that the direct rebound effect<br />
<strong>in</strong> this doma<strong>in</strong> is not negligible, with a “best guess” (Sorrell et al., 2009)<br />
between 10 <strong>and</strong> 30% .<br />
Our results <strong>in</strong>dicate an average direct rebound effect between 10 <strong>and</strong> 15%.<br />
Add<strong>in</strong>g the <strong>in</strong>direct rebound effect, we f<strong>in</strong>d an average total household rebound<br />
effect of 36%. It means that policy makers should not overestimate<br />
3
the power of efficiency to dim<strong>in</strong>ish energy consumption <strong>in</strong> the residential<br />
heat<strong>in</strong>g sector, because one third of the benefits of efficiency is lost through<br />
direct <strong>and</strong> <strong>in</strong>direct rebound effects. We also <strong>in</strong>vestigate who rebounds the<br />
most, <strong>and</strong> obta<strong>in</strong> among other that less educated people <strong>and</strong> people with a<br />
lower <strong>in</strong>come have a larger direct rebound effect.<br />
<strong>The</strong> rema<strong>in</strong>der of this article is structured as follows. In section 2, we provide<br />
an overview of how the rebound effect has been def<strong>in</strong>ed <strong>and</strong> measured <strong>in</strong> the<br />
literature, section 3 presents the data we use, <strong>and</strong> section 4 describes the<br />
models we estimate <strong>in</strong> section 5. Conclusions <strong>and</strong> policy implications are<br />
discussed <strong>in</strong> section 6.<br />
2 <strong>Rebound</strong> <strong>Effects</strong> <strong>in</strong> <strong>Residential</strong> <strong>Heat<strong>in</strong>g</strong><br />
Sorrell <strong>and</strong> Dimitropoulos (2008) provide an extensive discussion of the def<strong>in</strong>ition<br />
of the rebound effects (RE). <strong>The</strong> direct RE is basically def<strong>in</strong>ed as an<br />
<strong>in</strong>crease <strong>in</strong> the consumption of an energy service follow<strong>in</strong>g a decrease <strong>in</strong> the<br />
effective price of that service due to an improvement <strong>in</strong> the energy efficiency<br />
of deliver<strong>in</strong>g that service. Energy efficiency may be def<strong>in</strong>ed as ε = S/E, where<br />
E represents energy <strong>in</strong>put <strong>and</strong> S service dem<strong>and</strong>. In our study, S represents<br />
the services provided by heat<strong>in</strong>g. It is not only an <strong>in</strong>ternal temperature, but<br />
heat<strong>in</strong>g com<strong>for</strong>t <strong>in</strong> general. <strong>The</strong> rationale is that heat<strong>in</strong>g dem<strong>and</strong> may <strong>in</strong>crease<br />
because heat<strong>in</strong>g is turned on earlier <strong>in</strong> the season, or because of more<br />
frequent air<strong>in</strong>g, <strong>and</strong> not only because <strong>in</strong>ternal temperature is <strong>in</strong>creased.<br />
Us<strong>in</strong>g elasticities, the direct RE is def<strong>in</strong>ed as the elasticity of the service<br />
dem<strong>and</strong> (S) with respect to efficiency (ε):<br />
η ε (S) = ∂S<br />
∂ε · ε<br />
S<br />
(1)<br />
Because of the lack of data, this def<strong>in</strong>ition is seldom used <strong>in</strong> empirical studies.<br />
Authors usually rely on alternative def<strong>in</strong>itions such as the elasticity of the<br />
service dem<strong>and</strong> with respect to energy price. In the case of heat<strong>in</strong>g, an<br />
4
estimation of the price elasticity <strong>for</strong> heat<strong>in</strong>g fuel is often used <strong>in</strong> the literature<br />
to approximate the direct RE (Madlener <strong>and</strong> Hauertmann, 2011; Haas <strong>and</strong><br />
Biermayr, 2000). Yet, strong assumptions are needed to do so: people have<br />
to react symmetrically to a change <strong>in</strong> price <strong>and</strong> to a change <strong>in</strong> efficiency,<br />
an hypothesis rejected by Greene (2012) <strong>in</strong> the context of private mobility.<br />
Chan <strong>and</strong> Gill<strong>in</strong>gham (2015) criticize strongly this approach, demonstrat<strong>in</strong>g<br />
that it leads to biased estimations of rebound effects.<br />
In the present paper, we do not need to make such restrictive assumptions.<br />
We rely on a second def<strong>in</strong>ition of the RE, which is given by the proportion<br />
of the energy sav<strong>in</strong>gs which are not realised (as Chitnis et al., 2013, do), <strong>in</strong><br />
other words:<br />
<strong>Direct</strong> RE = 1 −<br />
Actual energy sav<strong>in</strong>gs<br />
Potential energy sav<strong>in</strong>gs<br />
(2)<br />
Note that def<strong>in</strong>itions (1) <strong>and</strong> (2) are equivalent s<strong>in</strong>ce Actual energy sav<strong>in</strong>gs =<br />
1 − η ε (S).<br />
<strong>The</strong>re is no consensus <strong>in</strong> the literature about the magnitude of the direct <strong>and</strong><br />
<strong>in</strong>direct rebound effects. For residential space heat<strong>in</strong>g, Sorrell et al. (2009)<br />
review the literature <strong>and</strong> collect estimates of the direct RE rang<strong>in</strong>g between<br />
10 <strong>and</strong> 58% <strong>in</strong> the short run <strong>and</strong> between 1.4 <strong>and</strong> 60% <strong>in</strong> the long run. <strong>The</strong>y<br />
suggest a mean value of 20% <strong>for</strong> the direct rebound effect <strong>for</strong> household<br />
heat<strong>in</strong>g. Nadel (2012), also <strong>in</strong> a review of the literature, advocates a likely<br />
range would be between 1 <strong>and</strong> 12%. He questions studies claim<strong>in</strong>g higher<br />
direct RE, because they are mostly based on price elasticity. In a recent<br />
article (Nadel, 2016), he summarizes the f<strong>in</strong>d<strong>in</strong>gs of studies look<strong>in</strong>g at both<br />
direct <strong>and</strong> <strong>in</strong>direct RE. For residential space heat<strong>in</strong>g, he f<strong>in</strong>ds that direct RE<br />
is generally about 10%, <strong>and</strong> <strong>in</strong>direct RE <strong>in</strong> the range of 10-20%, lead<strong>in</strong>g to<br />
a total rebound of 20 to 30%.<br />
We are not aware of any study that focuses on rebound effects <strong>in</strong> space<br />
heat<strong>in</strong>g <strong>in</strong> Switzerl<strong>and</strong>. In their study about the effects of global warm<strong>in</strong>g on<br />
energy use <strong>in</strong> Switzerl<strong>and</strong>, Gonseth et al. (2015) f<strong>in</strong>d a direct RE of 35% <strong>in</strong><br />
the long-run (up to 2060) us<strong>in</strong>g a CGE model. Madlener <strong>and</strong> Hauertmann<br />
5
(2011) <strong>and</strong> Haas <strong>and</strong> Biermayr (2000) <strong>in</strong>vestigate a similar topic <strong>for</strong> two<br />
neighbour<strong>in</strong>g countries, namely Germany <strong>and</strong> Austria. For Germany, a direct<br />
RE between 12 to 49% is found, with tenants hav<strong>in</strong>g a higher rebound than<br />
owners, <strong>and</strong> between 20 to 32% <strong>for</strong> Austria. <strong>The</strong>y both use price-elasticity.<br />
Some studies rely on eng<strong>in</strong>eer<strong>in</strong>g calculations, compar<strong>in</strong>g predicted energy<br />
use with observed energy use. For <strong>in</strong>stance Ayd<strong>in</strong> et al. (2014) study 500,000<br />
households <strong>in</strong> the Netherl<strong>and</strong>s, compar<strong>in</strong>g the energy label of dwell<strong>in</strong>gs with<br />
their energy consumption. <strong>The</strong>y f<strong>in</strong>d a direct RE of 28% <strong>for</strong> owners <strong>and</strong><br />
42% <strong>for</strong> tenants. This technique rely<strong>in</strong>g on eng<strong>in</strong>eer<strong>in</strong>g predictions has also<br />
been criticised, mostly because these predictions over-estimate the potential<br />
energy sav<strong>in</strong>gs of the efficiency improvements. Fowlie et al. (2015) study<br />
30,000 households participat<strong>in</strong>g <strong>in</strong> an energy efficiency program <strong>in</strong> the USA.<br />
<strong>The</strong>y f<strong>in</strong>d that the projected sav<strong>in</strong>gs by eng<strong>in</strong>eers are roughly 2.5 times the<br />
actual sav<strong>in</strong>gs. A part of this discrepancy may be due to direct RE. As they<br />
def<strong>in</strong>e it (an <strong>in</strong>crease <strong>in</strong> the <strong>in</strong>door temperature), they f<strong>in</strong>d no evidence <strong>for</strong><br />
it, attribut<strong>in</strong>g all the discrepancy to over-estimated eng<strong>in</strong>eer calculations.<br />
Although we argue <strong>in</strong> this article that direct RE is not only due to higher<br />
temperatures, a large part of the discrepancy rema<strong>in</strong>s expla<strong>in</strong>ed by overestimations<br />
of the eng<strong>in</strong>eers’ projections.<br />
<strong>The</strong> way we measure the direct RE, by us<strong>in</strong>g scenarios <strong>in</strong> a survey <strong>and</strong><br />
ask<strong>in</strong>g respondents about their reaction, is <strong>in</strong>novative <strong>in</strong> the field. It is the<br />
first time that this k<strong>in</strong>d of experiment is used to assess the rebound effect<br />
<strong>for</strong> residential heat<strong>in</strong>g. Only two authors previously used a survey <strong>in</strong> the<br />
rebound effect literature; Schleich et al. (2014) <strong>in</strong> Germany <strong>for</strong> lightn<strong>in</strong>g,<br />
<strong>and</strong> Yu et al. (2013) <strong>in</strong> Japan <strong>for</strong> vehicles.<br />
Most of the literature focuses solely on the direct RE, yet the <strong>in</strong>direct is<br />
also important <strong>for</strong> energy policies. <strong>The</strong> <strong>in</strong>direct rebound effect is l<strong>in</strong>ked<br />
to <strong>in</strong>come <strong>and</strong> substitution effects, although the latter is often put aside<br />
<strong>in</strong> the literature because it is considered as small (Thomas <strong>and</strong> Azevedo,<br />
2013a). We also consider only the <strong>in</strong>come effect, i.e., how the <strong>in</strong>come freed<br />
up by the efficiency improvement is spent. By spend<strong>in</strong>g it, overall energy<br />
consumption will decrease by less than the amount predicted by the efficiency<br />
6
improvement, as any product <strong>and</strong> service requires energy to be created <strong>and</strong><br />
used. To estimate this variation <strong>in</strong> energy consumption we take <strong>in</strong>to account<br />
not only the direct energy but also the embodied (grey) energy.<br />
Most of the studies on the <strong>in</strong>direct RE are based upon <strong>in</strong>come elasticities <strong>for</strong><br />
diverse categories of goods <strong>and</strong> services (Chitnis et al., 2013, <strong>for</strong> <strong>in</strong>stance) or<br />
<strong>in</strong>put-output tables (Thomas <strong>and</strong> Azevedo, 2013a; Lenzen <strong>and</strong> Dey, 2002).<br />
Data on the energy <strong>in</strong>tensity of the categories of goods <strong>and</strong> services are<br />
added to estimate the variation <strong>in</strong> energy consumption. Our estimation of<br />
the <strong>in</strong>direct RE is based on self-reported respend<strong>in</strong>g patterns <strong>and</strong> data on the<br />
embodied energy <strong>in</strong> kWh <strong>for</strong> categories of goods <strong>and</strong> services. We estimate<br />
at both the direct <strong>and</strong> the <strong>in</strong>direct RE, which very few studies have achieved<br />
be<strong>for</strong>e: Druckman et al. (2011) <strong>and</strong> Chitnis et al. (2013) conduct such analyses<br />
<strong>in</strong> terms of GHG emissions, f<strong>in</strong>d<strong>in</strong>g respectively a total rebound effect<br />
between 12 <strong>and</strong> 34% <strong>and</strong> between 5 <strong>and</strong> 15%.<br />
3 Data<br />
Our data come from an orig<strong>in</strong>al onl<strong>in</strong>e survey carried out <strong>in</strong> September 2015<br />
with 3,555 respondents representative of the Swiss population (exclud<strong>in</strong>g the<br />
Italian-speak<strong>in</strong>g region). Quotas match<strong>in</strong>g data from the Swiss Federal Office<br />
of Statistics were imposed <strong>for</strong> age, gender <strong>and</strong> region 1 . For <strong>in</strong>come levels we<br />
checked afterwards whether our sample was consistent with national data,<br />
<strong>and</strong> it differs only slightly (see figure A.4 <strong>in</strong> the appendix). <strong>The</strong> lowest <strong>and</strong><br />
the highest categories are under-represented <strong>in</strong> our sample. Yet we do not<br />
consider this as a problem <strong>in</strong> the estimation of the direct RE, s<strong>in</strong>ce we show<br />
later that both categories have an opposite effect on the magnitude of the<br />
direct RE. Thus it does not lead to a systematic upward or downward bias.<br />
<strong>The</strong> key questions of the survey regard<strong>in</strong>g the direct RE were asked us<strong>in</strong>g<br />
scenarios, which simulated an improvement <strong>in</strong> the efficiency of the heat<strong>in</strong>g<br />
1 Four regions represent the country: Rom<strong>and</strong>ie, Alps <strong>and</strong> Pre-Alps, Plateau West <strong>and</strong><br />
Plateau East.<br />
7
system. Each respondent was faced with three different scenarios: 1) a small<br />
improvement <strong>in</strong> efficiency (10, 15 or 20% r<strong>and</strong>omly chosen); 2) a large improvement<br />
(40, 50 or 60%); 3) a medium improvement (25 or 30%) aris<strong>in</strong>g<br />
from a CO 2 neutral technology. Under each scenario, we asked respondents<br />
whether they would modify their heat<strong>in</strong>g habits, <strong>and</strong> if yes by how much 2 .<br />
We used both qualitative <strong>and</strong> quantitative questions to ensure respondents<br />
understood the potential actions offered to them follow<strong>in</strong>g an efficiency improvement<br />
<strong>and</strong> to check they answered consistently.<br />
We should also acknowledge that our survey rules out superconservation (i.e.,<br />
negative rebound) <strong>and</strong> backfire (i.e., rebound larger than 100%) by design.<br />
Indeed, <strong>in</strong> the quantitative question, respondents were constra<strong>in</strong>ed to choose<br />
a number between 0 <strong>and</strong> the efficiency improvement <strong>in</strong> %. For <strong>in</strong>stance, if<br />
the scenario was based on an efficiency improvement of 20%, the scale of the<br />
slider along which respondents could make a choice went from 0 to 20 (like<br />
<strong>in</strong> figure A.2). We did so deliberately, <strong>in</strong> order to avoid potential confusion<br />
<strong>in</strong> the respondents, who would probably have wondered how such cases are<br />
possible. In light of the estimates of the direct rebound effect available <strong>in</strong><br />
the literature, most of which be<strong>in</strong>g around 20% <strong>and</strong> none be<strong>in</strong>g outside the<br />
range from 0 to 100%, we do not consider these constra<strong>in</strong>ts as a flaw of our<br />
design.<br />
To estimate the direct RE <strong>and</strong> to analyse who rebounds the most, we use<br />
a set of controls, namely education, <strong>in</strong>come, owner or tenant status, satisfaction<br />
regard<strong>in</strong>g heat<strong>in</strong>g com<strong>for</strong>t, environmental attitudes, <strong>and</strong> <strong>in</strong>door<br />
2 First, <strong>in</strong> a qualitative question, we provided possible reactions, such as sett<strong>in</strong>g the<br />
thermostat higher, air<strong>in</strong>g more often, or heat<strong>in</strong>g earlier/later <strong>in</strong> the season. This qualitative<br />
question was <strong>in</strong>tended to help the respondents th<strong>in</strong>k about the potential actions<br />
that have an impact on their fuel consumption related to heat<strong>in</strong>g <strong>and</strong> to frame them <strong>for</strong><br />
the next quantitative question. If at least one of the possible reactions was chosen, we<br />
requested the respondent to state how much of the sav<strong>in</strong>gs would be used to <strong>in</strong>crease heat<strong>in</strong>g<br />
services. Based on the def<strong>in</strong>ition of efficiency ε = S/E, we observe that when efficiency<br />
improves by ∆ε%, services will <strong>in</strong>crease by ∆ε% if energy consumption is kept constant,<br />
or energy consumption will decrease by ∆ε% if services are kept constant, <strong>and</strong> any other<br />
comb<strong>in</strong>ation with ∆S% − ∆E% = ∆ε% is possible. This is the range of possibilities we<br />
offer the respondents <strong>in</strong> the qualitative question. <strong>The</strong> questions relative to the direct RE<br />
are available <strong>in</strong> the appendix figures A.1 <strong>and</strong> A.2.<br />
8
temperature. Table 1 shows descriptive statistics <strong>for</strong> these variables.<br />
Table 1: Summary Statistics<br />
Variable Mean Std. dev. M<strong>in</strong>. Max. N<br />
Age 47.78 16.27 19 89 3,555<br />
Education 7.37 1.92 2 9 3,554<br />
Income level 3.97 1.41 1 6 2,924<br />
Female 0.51 0.50 0 1 3,555<br />
Tenants 0.58 0.49 0 1 3,555<br />
Environmental attitudes 22.88 6.41 0 36 3,543<br />
<strong>Heat<strong>in</strong>g</strong> satisfaction 10.40 3.22 0 15 3,477<br />
Indoor temperature 21.20 1.60 9 30 3,444<br />
Education goes from 1 (compulsory school not f<strong>in</strong>ished) to 9 (University <strong>and</strong><br />
higher vocational tra<strong>in</strong><strong>in</strong>g). Figure A.3 shows the frequencies. We group<br />
some levels together <strong>for</strong> the analysis, follow<strong>in</strong>g groups from the Federal Office<br />
of Statistics (FOS). <strong>The</strong> four groups are described <strong>in</strong> table A.1, as well as the<br />
percentage from the FOS. Compared to the whole population, people with a<br />
low education level (only compulsory school f<strong>in</strong>ished) are under-represented<br />
<strong>in</strong> our sample, <strong>and</strong> people with a high degree of education over-represented.<br />
This may slightly under-estimate the direct rebound effects, as we show <strong>in</strong><br />
the analysis that people less educated have a higher direct RE.<br />
<strong>Heat<strong>in</strong>g</strong> satisfaction is constructed as an <strong>in</strong>dex us<strong>in</strong>g the answers to five questions<br />
about the satisfaction on <strong>in</strong>ternal temperature <strong>in</strong> w<strong>in</strong>ter, uni<strong>for</strong>mity<br />
of temperature, quality of the ventilation, ease to modify the temperature<br />
<strong>and</strong> the number of days with the heat<strong>in</strong>g on. Respondents could be totally<br />
unsatisfied, rather unsatisfied, rather satisfied <strong>and</strong> totally satisfied of each<br />
item. To create the <strong>in</strong>dex, we attributed po<strong>in</strong>ts, respectively from 0 (totally<br />
unsatisfied) to 3 (totally satisfied). Consequently the respondent totally unsatisfied<br />
<strong>for</strong> the 5 items gets 0 po<strong>in</strong>t, whereas the respondent totally satisfied<br />
<strong>for</strong> the 5 items gets 15 po<strong>in</strong>ts. We proceeded <strong>in</strong> a similar way to build an<br />
<strong>in</strong>dex of environmental attitudes. Such an <strong>in</strong>dex has been used previously <strong>in</strong><br />
the literature, by Best <strong>and</strong> Mayerl (2013). N<strong>in</strong>e items were presented to the<br />
respondents who have to disagree-agree on a five-po<strong>in</strong>t scale. If the respon-<br />
9
dent completely disagrees with one item, he gets 0 po<strong>in</strong>t, if he completely<br />
agrees 4 po<strong>in</strong>ts. Hence the m<strong>in</strong>imal score is 0 (<strong>for</strong> those who care very little<br />
about environment) <strong>and</strong> the maximum is 36. <strong>The</strong> (stated) <strong>in</strong>door temperature<br />
goes from 9 to 30 degrees, but 96% of the answers lie between 18 <strong>and</strong> 25<br />
degrees. To dim<strong>in</strong>ish the impact of the outliers <strong>and</strong> because the answers are<br />
not cont<strong>in</strong>uous , we create three categories:
83 studies conta<strong>in</strong><strong>in</strong>g 616 stated-revealed preferences comparisons <strong>for</strong> quasipublic<br />
goods f<strong>in</strong>d that stated preferences estimates are smaller, but only<br />
slightly. However the downward bias is not systematic, <strong>and</strong> they conclude<br />
that there is no general need to correct stated preferences data. More recently,<br />
Grijalva et al. (2002) studied visitors’ behaviour <strong>in</strong> a climb<strong>in</strong>g area.<br />
<strong>The</strong>y f<strong>in</strong>d that <strong>in</strong>tended behaviour matches aggregate actual data. Loomis<br />
<strong>and</strong> Richardson (2006) exam<strong>in</strong>e the number of visits to a national park. <strong>The</strong>y<br />
conclude that the estimates from the stated <strong>and</strong> revealed preference methods<br />
are not statistically different from one another.<br />
To our knowledge, hypothetical choices have never been used to estimate direct<br />
rebound effect <strong>in</strong> the heat<strong>in</strong>g sector. In view of the literature compar<strong>in</strong>g<br />
stated <strong>and</strong> revealed preferences, we acknowledge that there may be a bias,<br />
but limited. To obta<strong>in</strong> results as robust as possible, we used two complementary<br />
strategies. First, we collected <strong>in</strong><strong>for</strong>mation on the rebound effect <strong>in</strong><br />
two different flavors, once through a qualitative question <strong>and</strong> once through<br />
a quantitative one. Based on these questions, we can dist<strong>in</strong>guish consistent<br />
<strong>and</strong> <strong>in</strong>consistent respondents, with the possibility to keep only the consistent<br />
ones <strong>for</strong> the analysis. Second, every respondent was faced with three different<br />
scenarios, under which he had to provide answers to the same questions.<br />
<strong>The</strong>se repeated questions allow us to build a panel. When controll<strong>in</strong>g <strong>for</strong><br />
<strong>in</strong>dividual heterogeneity <strong>in</strong> this way, our estimates will be based on changes<br />
with<strong>in</strong> <strong>in</strong>dividuals from one scenario to the other.<br />
Moreover there are many advantages <strong>in</strong> us<strong>in</strong>g stated preferences, Whitehead<br />
et al. (2008) summarize them. Stated preferences data are useful <strong>for</strong> the<br />
analysis of new policies, <strong>for</strong> which revealed preferences data do not exist.<br />
It is particularly relevant <strong>in</strong> the case of new policies lead<strong>in</strong>g to a change <strong>in</strong><br />
behaviour, <strong>in</strong> this case hypothetical choices may be the only way to gather<br />
<strong>in</strong><strong>for</strong>mation. Additionally, it <strong>in</strong>creases the sample size <strong>in</strong> a cross-section,<br />
as usually the respondents answer several times the hypothetical questions.<br />
<strong>The</strong>ir choices can be treated as panel data, provid<strong>in</strong>g more <strong>in</strong><strong>for</strong>mation about<br />
the preferences of each respondent.<br />
11
4 Empirical strategy<br />
We estimate the direct rebound effect us<strong>in</strong>g <strong>for</strong>mula (2). In the choice<br />
experiment of the survey, potential sav<strong>in</strong>gs are given. Respondents can subsequently<br />
choose the variation of service level, i.e., the part of the potential<br />
energy sav<strong>in</strong>gs which is taken back because of people’s reaction. Answers<br />
collected through this choice experiment thus provide all necessary data to<br />
apply <strong>for</strong>mula (2) directly: potential energy sav<strong>in</strong>gs are given by the efficiency<br />
improvement, while actual energy sav<strong>in</strong>gs are deduced from respondents’ answers.<br />
This strategy provides a different rebound effect <strong>for</strong> every <strong>in</strong>dividual<br />
<strong>and</strong> each scenario We use it to test <strong>for</strong> the impact of <strong>in</strong>dividual characteristics<br />
on its magnitude. <strong>The</strong> estimated equation is:<br />
<strong>Direct</strong> RE i,t = α + β 1 Educ i,t + β 2 Income i,t + β 3 F emale i,t<br />
+ β 4 Owner i,t + β 5 Environ i,t + β 6 Satisf i,t (3)<br />
+ β 7 T emperature i,t + β 8 Scenario i,t + u i<br />
Where i denotes the <strong>in</strong>dividual, t (= 1, 2, 3) denotes the scenario, <strong>and</strong> u is a<br />
r<strong>and</strong>om <strong>in</strong>tercept .<br />
Satisf is the score on the <strong>in</strong>dex of heat<strong>in</strong>g satisfaction <strong>and</strong> Environ the score<br />
on the environmental attitudes <strong>in</strong>dex. Income is divided <strong>in</strong> three classes<br />
(CHF): 9000. <strong>The</strong> variable Owner <strong>in</strong>dicates whether<br />
the <strong>in</strong>dividual owns or rents is residence <strong>and</strong> whether the heat<strong>in</strong>g bill is<br />
calculated on the <strong>in</strong>dividual consumption or shared among all the <strong>in</strong>habitants<br />
(calculated as a proportion of the m 2 of the home). Four categories exist <strong>for</strong><br />
this variable: owners with <strong>in</strong>dividual costs, owners with shared costs, tenants<br />
with <strong>in</strong>dividual costs, <strong>and</strong> tenants with shared costs. <strong>The</strong> rationale <strong>for</strong> that<br />
dist<strong>in</strong>ction is that tenants with <strong>in</strong>dividual costs should behave as owners.<br />
This hypothesis has never been tested be<strong>for</strong>e. Scenario is the small, middle<br />
(with the CO 2 neutral technology) or large efficiency improvement.<br />
We use a two-part model to estimate equation (3). As described by Belotti<br />
et al. (2015), a two-part model is appropriate when the outcome (y i ) has<br />
12
two features: 1) y i ≥ 0, <strong>and</strong> 2) y i = 0 is observed often enough. In our<br />
dataset, the direct RE is either zero or a positive value, with about half<br />
of the observations be<strong>in</strong>g zero. <strong>The</strong> two-part model accounts <strong>for</strong> the mass<br />
of zeroes by first fitt<strong>in</strong>g a b<strong>in</strong>ary choice model, <strong>and</strong> then, conditional on a<br />
positive outcome, fitt<strong>in</strong>g a l<strong>in</strong>ear regression model <strong>for</strong> the positive outcomes.<br />
Equation (3) is the second part of the two-part model. <strong>The</strong> first part is the<br />
b<strong>in</strong>ary choice model, <strong>and</strong> we use a probit model:<br />
P r(Y i,t = 1|X i,t ) = φ(X ′ i,tβ) (4)<br />
<strong>The</strong> vector X i ′ <strong>in</strong>cludes the same variables as <strong>in</strong> equation (3). In the two<br />
equations of the model we use panel data regression method. It is more efficient<br />
(lower st<strong>and</strong>ard errors) than pooled models, because the pooled model<br />
assumes <strong>in</strong>dependence over i <strong>and</strong> t. In our case, because all the <strong>in</strong>dependent<br />
variables are time-<strong>in</strong>variant, r<strong>and</strong>om effects are chosen. <strong>The</strong> r<strong>and</strong>om<br />
<strong>and</strong> <strong>in</strong>dividual <strong>in</strong>tercept u i accounts <strong>for</strong> autocorrelation due to the omitted<br />
time-<strong>in</strong>variant variables <strong>for</strong> a respondent.<br />
We expect a negative effect on the direct RE of education, <strong>in</strong>come, heat<strong>in</strong>g<br />
satisfaction <strong>and</strong> environmental attitude. It is obvious that people already<br />
fully satisfied with their heat<strong>in</strong>g com<strong>for</strong>t will be less prone to a direct RE,<br />
as well as people pay<strong>in</strong>g more attention to the environment. <strong>The</strong> effect<br />
of <strong>in</strong>come has been analysed <strong>in</strong> two previous studies (Chitnis et al., 2014;<br />
Madlener <strong>and</strong> Hauertmann, 2011), both f<strong>in</strong>d<strong>in</strong>g that richer people rebound<br />
less. An explanation is that they were not restrict<strong>in</strong>g their usage of heat<strong>in</strong>g<br />
be<strong>for</strong>e the efficiency improvement, <strong>and</strong> hence were already at their maximum<br />
level of com<strong>for</strong>t. Some evidence of the impact of <strong>in</strong>come on the rebound effect<br />
can also be found <strong>in</strong> macro-level studies <strong>and</strong> <strong>in</strong> various fields. For <strong>in</strong>stance,<br />
Small <strong>and</strong> Van Dender (2007) f<strong>in</strong>d that the rebound effect <strong>for</strong> motor vehicles<br />
decl<strong>in</strong>ed over 1966-2001 <strong>in</strong> the US, which they expla<strong>in</strong> by the rise <strong>in</strong><br />
<strong>in</strong>comes. More <strong>in</strong> general, rebound effect estimates are larger <strong>for</strong> develop<strong>in</strong>g<br />
countries than <strong>for</strong> developed ones, which is <strong>in</strong>terpreted as the impact of<br />
<strong>in</strong>come constra<strong>in</strong>ts <strong>in</strong> the <strong>for</strong>mer (e.g., Azevedo, 2014). <strong>The</strong>re<strong>for</strong>e, an <strong>in</strong>ter-<br />
13
est<strong>in</strong>g contribution of our paper is that we are able to determ<strong>in</strong>e the effect<br />
of <strong>in</strong>come on the rebound effect at the <strong>in</strong>dividual level. For education it is<br />
less obvious why less educated people would rebound more. A possibility is<br />
that they are less aware of the impact of their actions on the climate, there<strong>for</strong>e<br />
they will not restrict their heat<strong>in</strong>g usage <strong>for</strong> environmental concerns.<br />
F<strong>in</strong>ally we expect that the owners with shared or <strong>in</strong>dividual costs <strong>and</strong> the<br />
tenants with <strong>in</strong>dividual costs rebound more than the tenants with shared<br />
costs. <strong>The</strong> latter have fewer <strong>in</strong>centives to limit their heat<strong>in</strong>g usage <strong>and</strong> then<br />
could already have reached a maximum heat<strong>in</strong>g com<strong>for</strong>t prior to the efficiency<br />
improvement. Madlener <strong>and</strong> Hauertmann (2011) f<strong>in</strong>d that tenants rebound<br />
more than owners, but they do not exam<strong>in</strong>e the features of the heat<strong>in</strong>g bill.<br />
For temperature we expect a negative coefficient, as people gets closer to<br />
their satiety po<strong>in</strong>t.<br />
With the scenario dummies, we test whether the direct RE is l<strong>in</strong>ear with the<br />
efficiency improvement, i.e., whether a larger improvement would <strong>in</strong>duce a<br />
larger direct RE. <strong>The</strong> green technology <strong>in</strong> the second scenario is used to see<br />
whether people react more (have a larger direct RE) if on top of the efficiency<br />
improvement they benefit from a green technology. <strong>The</strong> hypothesis is that<br />
people would react more because they get rid of a sort of guilt of consum<strong>in</strong>g<br />
more of a pollut<strong>in</strong>g service. We also tested <strong>for</strong> the impact of other variables:<br />
age, the region, the hous<strong>in</strong>g type, the size of the house or flat, the size of the<br />
household, the number of children, rural or urban household. None of them<br />
was significant.<br />
5 Results<br />
5.1 Estimations <strong>and</strong> Analysis of the <strong>Direct</strong><br />
<strong>Rebound</strong> Effect<br />
<strong>The</strong> implementation of <strong>for</strong>mula (2) gives an <strong>in</strong>dividual RE <strong>for</strong> each respondent<br />
<strong>in</strong> each scenario, i.e., three estimates <strong>for</strong> every respondent. <strong>The</strong> overall<br />
14
esults are very similar <strong>for</strong> the three scenarios, with an average direct RE estimated<br />
between 10 <strong>and</strong> 15%. When the three scenarios are pooled together,<br />
the average direct RE is 12.2%. Table 2 reports the values obta<strong>in</strong>ed <strong>and</strong><br />
figure A.5 displays the distribution of the strictly positive values. A direct<br />
RE of 12.2% is rather <strong>in</strong> the low-end of the estimations obta<strong>in</strong>ed so far <strong>in</strong><br />
the literature, but it is consistent with the reviews by Sorrell et al. (2009)<br />
(10-30%) <strong>and</strong> Nadel (2016) (1-12%).<br />
Table 2:<br />
Estimation of the <strong>Direct</strong> <strong>Rebound</strong> Effect<br />
Mean Std. dev. M<strong>in</strong>. Max. N<br />
<strong>Direct</strong> RE (Small eff. improvement) 0.147 0.226 0 1 3,555<br />
<strong>Direct</strong> RE (Large eff. improvement) 0.106 0.187 0 1 3,555<br />
<strong>Direct</strong> RE (Middle eff. imp. + CO 2 neutral) 0.113 0.193 0 1 3,555<br />
<strong>Direct</strong> RE: pooled 0.122 0.203 0 1 10,665<br />
Note: <strong>The</strong> means are calculated us<strong>in</strong>g <strong>for</strong>mula (2) <strong>and</strong> can be multiplied by 100<br />
to obta<strong>in</strong> to direct RE <strong>in</strong> %. About half of the respondents have a zero direct RE.<br />
In the literature, the only possibility usually considered <strong>for</strong> a direct RE <strong>in</strong><br />
heat<strong>in</strong>g is an <strong>in</strong>crease <strong>in</strong> the temperature. Yet, people can react to an efficiency<br />
improvement <strong>in</strong> various ways, <strong>for</strong> <strong>in</strong>stance by air<strong>in</strong>g more often their<br />
house, or start<strong>in</strong>g to heat earlier <strong>in</strong> the season, etc. <strong>The</strong> purpose of the qualitative<br />
question <strong>in</strong> the survey is precisely to <strong>in</strong>vestigate such possibilities. <strong>The</strong><br />
question is made of 5 items about the hypothetical change <strong>in</strong> behaviour, with<br />
three possible choices: no, maybe, yes. Figure A.6 <strong>in</strong> the appendix shows<br />
the answers. Air<strong>in</strong>g longer <strong>and</strong> more frequently is <strong>in</strong>deed what respondents<br />
chose the more often, be<strong>for</strong>e pay<strong>in</strong>g less attention to heat<strong>in</strong>g <strong>in</strong> general. Increas<strong>in</strong>g<br />
temperature only comes as the third most popular choice. It shows<br />
that by consider<strong>in</strong>g only the <strong>in</strong>crease <strong>in</strong> temperature, the direct RE will be<br />
underestimated (see also Voll<strong>and</strong>, 2016).<br />
15
One concern with data com<strong>in</strong>g from a choice experiment is to make sure<br />
that respondents understood correctly the questions. In our sett<strong>in</strong>g, we can<br />
control <strong>for</strong> that by compar<strong>in</strong>g<br />
answers to the qualitative question on the<br />
rebound effect (an easy question) <strong>and</strong> to the quantitative question (more<br />
difficult). We attributed zero, one <strong>and</strong> two po<strong>in</strong>ts to the qualitative question<br />
(no, maybe, yes) to obta<strong>in</strong> an overall view of the changes <strong>in</strong> the heat<strong>in</strong>g<br />
habits. Hence, more po<strong>in</strong>ts <strong>in</strong>dicate more substantial modifications of habits<br />
<strong>and</strong> a larger direct rebound effect. Someone who would change noth<strong>in</strong>g gets<br />
0 po<strong>in</strong>t. Table 3 highlights that respondents answered consistently to both<br />
questions. <strong>The</strong> more they decided to change <strong>in</strong> the qualitative question, the<br />
largest changes they reported <strong>in</strong> the quantitative question.<br />
Table 3: Consistency <strong>in</strong> the stated preferences<br />
Qualitative RE 0 1 2 3 4 5 6<br />
Quantitative RE 0% 17% 21% 26% 29.8% 33.9% 32.8%<br />
Respondents with 0 po<strong>in</strong>t <strong>in</strong> the qualitative question get mechanically a direct RE<br />
of zero as the quantitative question did not appear <strong>for</strong> them. <strong>The</strong> qualitative RE is<br />
an <strong>in</strong>dex, while the quantitative rebound is estimated with equation (2).<br />
By compar<strong>in</strong>g the answers of each respondent to the qualitative <strong>and</strong> quantitative<br />
questions, we can def<strong>in</strong>e who is <strong>in</strong>consistent. An <strong>in</strong>consistent respondent<br />
is someone who said <strong>in</strong> the qualitative question that he would change his heat<strong>in</strong>g<br />
behaviour along at least one dimension, but did not report any change<br />
<strong>in</strong> the correspond<strong>in</strong>g quantitative question. Hence <strong>for</strong> him the quantitative<br />
direct rebound we calculate is zero, while his qualitative rebound is non-zero.<br />
It is likely that he did not underst<strong>and</strong> well the quantitative question, or he<br />
was not able to answer it. Inconsistent respondents are less educated <strong>and</strong><br />
have a lower <strong>in</strong>come than the average. As a robustness check, we per<strong>for</strong>m<br />
our analysis by exclud<strong>in</strong>g them. It does not change significantly our results.<br />
Once the direct RE estimated <strong>for</strong> each <strong>in</strong>dividual, we can assess which characteristics<br />
<strong>in</strong>fluence the magnitude of the direct RE, or who rebounds the<br />
most. This is <strong>in</strong>vestigated us<strong>in</strong>g equation (3) with a two-part model, whose<br />
results are reported <strong>in</strong> table 4). For the first part of the model (a probit es-<br />
16
timation), we report the marg<strong>in</strong>al effects at the means. <strong>The</strong> marg<strong>in</strong>al effects<br />
<strong>in</strong>dicate the <strong>in</strong>crease <strong>in</strong> the probability of hav<strong>in</strong>g a positive direct rebound<br />
(versus a zero direct rebound) associated with a one-unit <strong>in</strong>crease of the correspond<strong>in</strong>g<br />
variables. Only respondents with a positive direct RE are kept <strong>for</strong><br />
the second part, <strong>and</strong> the coefficients <strong>in</strong> this estimation are to be <strong>in</strong>terpreted<br />
as the <strong>in</strong>crease <strong>in</strong> the magnitude of the direct rebound follow<strong>in</strong>g a one-unit<br />
<strong>in</strong>crease of the correspond<strong>in</strong>g variable.<br />
In both estimations, education <strong>and</strong> <strong>in</strong>come have the expected negative sign.<br />
For <strong>in</strong>stance, people with the highest level of education have a 20% lower<br />
probability to have a positive direct rebound, compared to people who stopped<br />
at compulsory school. However the effect of education is not significant <strong>in</strong><br />
the l<strong>in</strong>ear regression. Be<strong>in</strong>g a woman decreases both the probability <strong>and</strong><br />
the magnitude of the direct RE. Environmental attitudes <strong>and</strong> heat<strong>in</strong>g satisfaction<br />
also have the expected negative sign: an <strong>in</strong>crease <strong>in</strong> one st<strong>and</strong>ard<br />
deviation <strong>for</strong> environmental attitudes leads to a decrease by 4% <strong>in</strong> the probability<br />
of direct rebound, <strong>for</strong> heat<strong>in</strong>g satisfaction it is by 8%. People more<br />
environmentally conscious have also a lower direct RE.<br />
<strong>The</strong> coefficients related to <strong>in</strong>door temperature are unexpectedly positive. It<br />
is robust even if we change the choice of the degrees <strong>in</strong> the categories, <strong>and</strong><br />
also if we drop the outliers (less than 17 degrees or more than 25). However<br />
if the reference category is (19.5-22.5), the last category is not significantly<br />
different. Our <strong>in</strong>terpretation is that a part of the people with a low <strong>in</strong>door<br />
temperature have a preference <strong>for</strong> this <strong>and</strong> will not change even if the service<br />
is cheaper. A question <strong>in</strong> the survey is “Would you be will<strong>in</strong>g to dim<strong>in</strong>ish<br />
the temperature <strong>in</strong> w<strong>in</strong>ter?” <strong>The</strong>y are 56% answer<strong>in</strong>g that they already<br />
do it, versus 38 <strong>and</strong> 20% respectively <strong>for</strong> the middle <strong>and</strong> high temperature<br />
categories.<br />
<strong>The</strong> negative signs on the magnitude of the efficiency improvement shows that<br />
people rebound, but up to a certa<strong>in</strong> po<strong>in</strong>t <strong>and</strong> not <strong>in</strong>def<strong>in</strong>itely. Imag<strong>in</strong>e you<br />
would feel more com<strong>for</strong>table if you heat your home slightly more, <strong>for</strong> <strong>in</strong>stance<br />
us<strong>in</strong>g 15% more of heat<strong>in</strong>g energy. <strong>The</strong>n if the efficiency improvement is 15%<br />
you have a direct RE of 100%, but if the efficiency improvement is 50% your<br />
17
Table 4:<br />
Two-part model <strong>for</strong> the <strong>Direct</strong> RE<br />
Probit model, MEs<br />
L<strong>in</strong>ear regression<br />
Apprenticeship −0.151 ** −0.037<br />
(0.076) (0.042)<br />
Baccalaureate −0.186 ** −0.036<br />
(0.079) (0.044)<br />
University <strong>and</strong> higher vocational<br />
tra<strong>in</strong><strong>in</strong>g<br />
−0.200 *** −0.067<br />
(0.076) (0.042)<br />
Income 4500-9000 −0.029 −0.025 *<br />
(0.023) (0.014)<br />
Income >9000 −0.074 *** −0.023<br />
(0.025) (0.015)<br />
Female −0.035 ** −0.035 ***<br />
(0.017) (0.010)<br />
Owners shared costs 0.032 0.044 **<br />
(0.035) (0.021)<br />
Tenants shared costs −0.029 −0.015<br />
(0.023) (0.014)<br />
Tenants <strong>in</strong>dividual costs −0.002 0.004<br />
(0.021) (0.013)<br />
Environmental attitudes −0.006 *** −0.002 ***<br />
(0.001) (0.001)<br />
<strong>Heat<strong>in</strong>g</strong> satisfaction −0.024 *** −0.002<br />
(0.003) (0.002)<br />
19.5-22.5 degrees 0.066 ** −0.005<br />
(0.029) (0.019)<br />
>22.5 degrees 0.089 *** 0.004<br />
(0.034) (0.021)<br />
Large eff. improv. −0.020 ** −0.079 ***<br />
(0.008) (0.005)<br />
Middle eff. improv. + CO2 neutral −0.033 *** −0.057 ***<br />
(0.008) (0.005)<br />
Constant − 0.468 ***<br />
#Obs. 8, 391 3, 812<br />
Note: St<strong>and</strong>ard errors <strong>in</strong> parentheses. ∗ p < .1, ∗∗ p < .05, ∗∗∗<br />
p < .01<br />
<strong>The</strong> dependent variable is the direct RE as estimated with <strong>for</strong>mula<br />
(2).<br />
18<br />
(0.054)
direct RE is only 30% (= 15/50). Here the magnitude of the improvement<br />
decreases both the probability to rebound <strong>and</strong> the magnitude of the direct<br />
rebound. In the probit model, the scenario with the middle improvement<br />
<strong>and</strong> the CO 2 neutral technology leads to a higher decrease <strong>in</strong> probability<br />
of rebound than the large efficiency improvement (the two coefficients are<br />
statistically different at the 10% level). Contrary to what was expected, the<br />
green technology does not seem to lead to a higher direct rebound, but rather<br />
to a decrease <strong>in</strong> the probability of rebound. On the magnitude of the rebound,<br />
the effect is not clear. Some people rebound only <strong>in</strong> this third scenario,<br />
but they are only 116 respondents (3.3% of the sample). Interest<strong>in</strong>gly, a<br />
probit model shows that environmental attitudes as well as a low <strong>in</strong>door<br />
temperature <strong>in</strong>crease the likelihood of belong<strong>in</strong>g to this group of respondents.<br />
It thus seems that a “green rebound” does exist, but only a marg<strong>in</strong>al one.<br />
Hypotheses on who will rebound the most have often been made <strong>in</strong> previous<br />
research, but very rarely tested due to the lack of data. We here show that<br />
education, <strong>in</strong>come, environmental attitudes <strong>and</strong> heat<strong>in</strong>g staisfaction decrease<br />
the probability of the direct rebound effect. Our f<strong>in</strong>d<strong>in</strong>gs highlight important<br />
facts: First, the magnitude of the direct RE is very heterogeneous among<br />
people. Second, the direct RE depends on the level of the efficiency improvement,<br />
large improvements do not mechanically imply a higher rebound than<br />
smaller improvements. Third, measures target<strong>in</strong>g low <strong>in</strong>come households (<strong>for</strong><br />
<strong>in</strong>stance subsidies conditional on <strong>in</strong>come) will be less effective <strong>in</strong> terms of energy<br />
saved, because they are associated with larger rebound effects. Chitnis<br />
et al. (2014), by us<strong>in</strong>g expenditure elasticities <strong>for</strong> different socio-economic<br />
groups, have reached similar conclusions concern<strong>in</strong>g <strong>in</strong>come.<br />
5.2 Estimation <strong>and</strong> Analysis of the <strong>Indirect</strong><br />
<strong>Rebound</strong> Effect<br />
To estimate the <strong>in</strong>direct RE, we use the answers to the re-spend<strong>in</strong>g question<br />
(i.e., how<br />
respondents would allocate CHF 1,000 saved on heat<strong>in</strong>g among<br />
19
n<strong>in</strong>e categories of goods <strong>and</strong> services) <strong>and</strong> the embodied energy <strong>for</strong> each<br />
category. Potential sav<strong>in</strong>gs are calculated as the amount of embodied energy<br />
saved when spend<strong>in</strong>g CHF 1,000 less on heat<strong>in</strong>g: 1,000 [CHF] × 10.64<br />
[kWh/CHF] = 10,640 [kWh] (see figure A.7 <strong>in</strong> appendix). We then compute<br />
the emodied energy amount consumed when re-spend<strong>in</strong>g the CHF 1,000 on<br />
various categories of goods. We thus have potential <strong>and</strong> actual sav<strong>in</strong>gs <strong>for</strong><br />
each household, which allows us to apply <strong>for</strong>mula 2 <strong>and</strong> retrieve an estimation<br />
of the <strong>in</strong>direct rebound effect.<br />
We obta<strong>in</strong> an average <strong>in</strong>direct RE of 24.7%. This result means that on<br />
top of the direct RE, about a quarter of the potential energy sav<strong>in</strong>gs are<br />
lost due to the re-spend<strong>in</strong>g of the sav<strong>in</strong>gs <strong>in</strong>itially made on heat<strong>in</strong>g. <strong>The</strong><br />
distribution of the <strong>in</strong>dividual <strong>in</strong>direct RE is shown <strong>in</strong> appendix figure A.8.<br />
<strong>The</strong> median rebound effect is at 14.5% <strong>and</strong> the largest values are above<br />
100%, which corresponds to a backfire situation because the <strong>in</strong>dividual ends<br />
up consum<strong>in</strong>g more energy than be<strong>for</strong>e the efficiency improvement. Such a<br />
situation is possible if a large part of the sav<strong>in</strong>gs made on heat<strong>in</strong>g is used<br />
<strong>for</strong> additional air travel.<br />
As <strong>for</strong> the direct RE, we can assess which personal characteristics have an<br />
impact on the magnitude of the <strong>in</strong>direct RE. However, there is an important<br />
difference with the direct RE, <strong>in</strong> the sense that the <strong>in</strong>direct RE is less salient<br />
<strong>and</strong> tangible <strong>for</strong> people because we take <strong>in</strong>to account the grey (embodied)<br />
energy. <strong>The</strong>y may know that travell<strong>in</strong>g by plane or driv<strong>in</strong>g their car is energy<br />
<strong>in</strong>tensive, but they are much less likely to know whether go<strong>in</strong>g to a restaurant<br />
is more or less energy <strong>in</strong>tensive than buy<strong>in</strong>g clothes.<br />
In our model, we <strong>in</strong>clude similar determ<strong>in</strong>ants as <strong>in</strong> equation (3): socioeconomic<br />
characteristics, environmental attitudes, <strong>and</strong> tenant/owner status.<br />
Furthermore, <strong>in</strong> order to <strong>in</strong>vestigate potential l<strong>in</strong>ks between the direct <strong>and</strong><br />
<strong>in</strong>direct rebound effect, we <strong>in</strong>clude the direct rebound effect estimated earlier<br />
<strong>in</strong> the determ<strong>in</strong>ants of the <strong>in</strong>direct rebound effect. In theory, there is an<br />
automatic negative l<strong>in</strong>k between the direct <strong>and</strong> <strong>in</strong>direct RE, because the<br />
larger the direct RE, the lowest the rema<strong>in</strong><strong>in</strong>g sav<strong>in</strong>gs to spend on other goods<br />
(Thomas <strong>and</strong> Azevedo, 2013b). However there could be other l<strong>in</strong>ks between<br />
20
the two RE, <strong>for</strong> <strong>in</strong>stance if people car<strong>in</strong>g very few about the environment<br />
would display both a large direct RE <strong>and</strong> a large <strong>in</strong>direct RE. Thanks to the<br />
design of our survey, this automatic l<strong>in</strong>k is absent, <strong>and</strong> we are able to study<br />
an empirical <strong>and</strong> unconstra<strong>in</strong>ed relation that could potentilly exists between<br />
the direct <strong>and</strong> the <strong>in</strong>direct RE. We use the natural logarithm of the <strong>in</strong>direct<br />
RE to dim<strong>in</strong>ish the impact of the long right tail <strong>in</strong> the distribution. <strong>The</strong><br />
model is:<br />
ln (<strong>Indirect</strong> RE i ) = α + β 1 <strong>Direct</strong> RE i + β 2 Educ i<br />
+ β 3 Income i + β 4 Environ i + β 5 Owner i + ε i (5)<br />
We expect a negative coefficient <strong>for</strong> environmental attitudes, as people with<br />
green values pay probably more attention to the CO 2 footpr<strong>in</strong>t of their consumption.<br />
For the other explanatory variables, we do not make any hypothesis.<br />
<strong>The</strong> results are presented <strong>in</strong> table 5.<br />
<strong>The</strong> environmental attitudes have the expected negative sign. By compar<strong>in</strong>g<br />
the re-spend<strong>in</strong>g patterns of people <strong>in</strong> the first quartile <strong>and</strong> the last quartile<br />
of the environmental attitudes, we observe that people <strong>in</strong> the first quartile<br />
re-spend more on air travel, car fuel <strong>and</strong> electrical appliances, <strong>and</strong> less on<br />
public transport <strong>and</strong> leisure. <strong>The</strong> differences were tested with t-tests on the<br />
means. Tenants have a higher <strong>in</strong>direct RE than owners, <strong>and</strong> now the type<br />
of the heat<strong>in</strong>g bill does not matter any more. <strong>The</strong> ma<strong>in</strong> difference <strong>in</strong> the<br />
re-spend<strong>in</strong>g patterns of tenants is that they choose to allocate less to sav<strong>in</strong>gs<br />
than owners, <strong>and</strong> as sav<strong>in</strong>gs have a low embodied energy it expla<strong>in</strong>s why they<br />
have a larger <strong>in</strong>direct RE.<br />
<strong>The</strong> positive coefficient of the direct RE shows that the larger the direct RE,<br />
the larger the <strong>in</strong>direct one. <strong>The</strong> ma<strong>in</strong> difference <strong>in</strong> terms of re-spend<strong>in</strong>g<br />
patterns between people who never rebound <strong>and</strong> those who always rebound,<br />
is that the latter save less money. <strong>The</strong>y also re-spend a larger part on air<br />
travel <strong>and</strong> car fuel.<br />
21
Table 5: <strong>Indirect</strong> <strong>Rebound</strong> Effect<br />
<strong>Direct</strong> RE 0.212 ***<br />
(0.057)<br />
Apprenticeship 0.188<br />
(0.117)<br />
Baccalaureate 0.247 **<br />
(0.122)<br />
University <strong>and</strong> higher 0.188<br />
(0.117)<br />
Income 4500-9000 −0.037<br />
(0.037)<br />
Income >9000 −0.066 *<br />
(0.039)<br />
Environmental attitudes −0.008 ***<br />
(0.002)<br />
Owners shared costs 0.060<br />
(0.055)<br />
Tenants shared costs 0.123 ***<br />
(0.034)<br />
Tenants <strong>in</strong>dividual costs 0.124 ***<br />
(0.031)<br />
Constant −1.774 ***<br />
#Obs. 2, 822<br />
L<strong>in</strong>ear regression<br />
(0.129)<br />
Note: St<strong>and</strong>ard errors <strong>in</strong> parentheses. * p < 0.10, ** p < 0.05, *** p < 0.01.<br />
<strong>The</strong> dependent variable is the natural logarithm of the <strong>in</strong>direct RE.<br />
22
5.3 Estimation of the Total Microeconomic<br />
Household <strong>Rebound</strong> Effect<br />
To compute the total household rebound effect we add up the direct <strong>and</strong><br />
<strong>in</strong>direct rebound effects. We obta<strong>in</strong> an average total household RE of 36.7%<br />
with a median at 23.2%. Figure A.9 <strong>in</strong> appendix shows the distribution of<br />
this total RE.<br />
Our ma<strong>in</strong> f<strong>in</strong>d<strong>in</strong>g is that, <strong>in</strong> the doma<strong>in</strong> of residential heat<strong>in</strong>g, about one<br />
third of the energy sav<strong>in</strong>gs (<strong>in</strong> terms of kWh) <strong>in</strong>itially expected after an<br />
efficiency improvement is lost due to the direct <strong>and</strong> <strong>in</strong>direct rebound effects.<br />
However, heterogeneity is large, <strong>and</strong> this total household RE is an average.<br />
Very few studies use the same dataset to estimate direct <strong>and</strong> <strong>in</strong>direct RE<br />
together. One comparable result is from Chitnis et al. (2014) <strong>for</strong> the UK.<br />
Us<strong>in</strong>g expenditure elasticities, they f<strong>in</strong>d a rebound effect (direct <strong>and</strong> <strong>in</strong>direct)<br />
between 0 <strong>and</strong> 32% but <strong>in</strong> terms of greenhouse gas.<br />
6 Conclusion<br />
In this paper we estimate the rebound effect <strong>in</strong> residential heat<strong>in</strong>g <strong>in</strong> Switzerl<strong>and</strong><br />
at the household level, <strong>in</strong>clud<strong>in</strong>g both direct <strong>and</strong> <strong>in</strong>direct rebound effects<br />
(RE). <strong>Direct</strong> RE arises when households adapt to an improvement <strong>in</strong><br />
efficiency of their heat<strong>in</strong>g system by <strong>in</strong>creas<strong>in</strong>g their dem<strong>and</strong> <strong>for</strong> heat<strong>in</strong>g services.<br />
<strong>The</strong> rationale is as follows: improved efficiency means a cheaper service,<br />
then why not consume more of this service? Us<strong>in</strong>g an orig<strong>in</strong>al dataset<br />
created <strong>for</strong> this purpose, we estimate an average direct RE between 10 <strong>and</strong><br />
15%. It means that only 85-90% of the energy sav<strong>in</strong>gs expected after an<br />
efficiency improvement from an eng<strong>in</strong>eer<strong>in</strong>g perspective are <strong>in</strong> fact realised.<br />
This result is not too worry<strong>in</strong>g <strong>for</strong> policy makers who can still count on<br />
efficiency to play a major role <strong>in</strong> the energy transition. However to see the<br />
whole picture, one should also take the <strong>in</strong>direct rebound effect <strong>in</strong>to account.<br />
<strong>Indirect</strong> RE stems from the sav<strong>in</strong>gs made on heat<strong>in</strong>g after an improvement <strong>in</strong><br />
23
efficiency, <strong>and</strong> which are re-spent <strong>in</strong> various activities. Purchas<strong>in</strong>g any good<br />
or service implies the consumption of energy, because every good <strong>and</strong> service<br />
consumes energy <strong>in</strong> order to be produced <strong>and</strong> used. Even bank sav<strong>in</strong>gs<br />
use energy as they are lent <strong>for</strong> some other purposes. As the majority of<br />
goods <strong>and</strong> services are less energy <strong>in</strong>tensive than heat<strong>in</strong>g, overall energy<br />
consumption will generally decrease after an improvement <strong>in</strong> efficiency of<br />
the heat<strong>in</strong>g system, except if the money saved is used on a very energy<br />
<strong>in</strong>tensive good (such as travell<strong>in</strong>g by plane). In such cases, overall energy<br />
consumption may even <strong>in</strong>crease, which is called a backfire effect or <strong>in</strong> other<br />
words a rebound effect of more than 100%.<br />
Our analysis shows that backfire is extremely rare <strong>and</strong> that the average total<br />
household rebound effect (the direct + <strong>in</strong>direct RE) is around 36%. This<br />
amount is not negligible, <strong>and</strong> means that about one third of the energy<br />
sav<strong>in</strong>gs <strong>in</strong>itially expected is lost due to the direct <strong>and</strong> <strong>in</strong>direct rebound effects.<br />
For policy makers <strong>in</strong> charge of the energy transition it means that the role<br />
of efficiency improvement is currently probably overestimated.<br />
Our study also highlights the large heterogeneity of the magnitude of the<br />
direct <strong>and</strong> <strong>in</strong>direct RE among <strong>in</strong>dividuals. Those who are affluent, educated,<br />
satisfied with their heat<strong>in</strong>g com<strong>for</strong>t, <strong>and</strong> environmentally conscious are less<br />
prone to have a direct rebound. We show <strong>for</strong> <strong>in</strong>stance that people with a<br />
lower <strong>in</strong>come have a larger direct rebound effect. As a consequence, measures<br />
target<strong>in</strong>g those people will be less effective <strong>in</strong> terms of energy saved. F<strong>in</strong>ally<br />
we also show that the level of efficiency improvement impacts negatively the<br />
direct rebound, i.e., it is not because you face a large efficiency improvement<br />
that you will rebound more.<br />
24
Appendix A<br />
Appendix<br />
Figure A.1: <strong>The</strong> qualitative question about the direct RE<br />
Note: <strong>The</strong> scenario is presented be<strong>for</strong>e, with the efficiency improvement <strong>and</strong> the<br />
costs saved given <strong>in</strong> % of their current heat<strong>in</strong>g costs.<br />
Figure A.2: <strong>The</strong> quantitative question about the direct RE<br />
Note: <strong>The</strong> slider is constra<strong>in</strong>ed to be at the maximum equal to the efficiency<br />
improvement <strong>in</strong> %.<br />
25
Figure A.3: Level of education<br />
Compulsory school<br />
School of commerce/household school<br />
Elementary vocational tra<strong>in</strong><strong>in</strong>g<br />
Apprenticeship<br />
Diploma<br />
Full−time vocational school<br />
Baccalaureate<br />
University <strong>and</strong> higher vocational tra<strong>in</strong><strong>in</strong>g<br />
0 200 400 600 800 1,000 1,200 1,400 1,600 1,800<br />
Frequency<br />
Note: Highest degree of education achieved by the respondent.<br />
Table A.1: Level of education <strong>in</strong> four categories<br />
Education Freq. Percent Percent <strong>in</strong> Switzerl<strong>and</strong><br />
Compulsory school 41 1.15 11.9<br />
Apprenticeship, diploma, etc. 1, 338 37.65 38.25<br />
High school 382 10.75 8.25<br />
University <strong>and</strong> higher vocational tra<strong>in</strong><strong>in</strong>g 1, 793 50.45 41.65<br />
<strong>The</strong> percent <strong>in</strong> Switzerl<strong>and</strong> comes from the Federal Office of Statistics <strong>for</strong> 2015.<br />
<strong>The</strong> category apprenticeship,... <strong>in</strong>cludes all the categories between compulsory school <strong>and</strong> baccalaureate.<br />
26
Figure A.4: Household gross <strong>in</strong>come <strong>in</strong> the sample versus at the national<br />
level<br />
Note: <strong>Rebound</strong> st<strong>and</strong>s <strong>for</strong> the sample of the survey, SHP <strong>for</strong> the Swiss Household<br />
Panel. <strong>The</strong> SHP provides data on the gross <strong>in</strong>come at the household level.<br />
27
Figure A.5: <strong>Direct</strong> RE<br />
Density<br />
0 4.622<br />
Median<br />
0 .2 .4 .6 .8 1<br />
<strong>Direct</strong> RE (n=4’808)<br />
Note: <strong>The</strong> average direct RE is 12.2%. In the histogram the zero-rebound are<br />
dropped, they count <strong>for</strong> about half of the observations.<br />
28
Figure A.6: Qualitative question: changes <strong>in</strong> behaviour<br />
0 500 1,000 1,500 2,000 2,500 3,000 3,500<br />
Increase temp. Sooner/later <strong>in</strong> the year Air<strong>in</strong>g Less attention No decrease if absent<br />
Maybe<br />
Not:Note: Over 10,665 answers (3 answers per respondent). For the last category:<br />
over 7,793 answers.<br />
Yes<br />
29
15<br />
14.57<br />
Figure A.7: Energy Intensity <strong>in</strong> kWh/CHF<br />
13.90<br />
10<br />
10.24<br />
kWh/CHF<br />
6.96<br />
5<br />
2.61<br />
0<br />
1.75 1.61 1.36 1.21<br />
0.92<br />
0.29<br />
Electricity<br />
Air travel<br />
<strong>Heat<strong>in</strong>g</strong><br />
Car fuel<br />
Food <strong>and</strong> beverages<br />
Public transport<br />
Leisure <strong>and</strong> eat<strong>in</strong>g out<br />
Electrical appliances<br />
Other goods<br />
Other services<br />
Clothes <strong>and</strong> shoes<br />
Note: Embodied energy from LCA data. Source: Eco<strong>in</strong>vent (Zürich), <strong>and</strong> Ivan<br />
Tilov (University of Neuchâtel).<br />
30
0<br />
Density<br />
10.67<br />
Median<br />
Figure A.8: <strong>Indirect</strong> RE<br />
0 .2 .4 .6 .8 1 1.2 1.4<br />
Note: <strong>The</strong> average <strong>in</strong>direct RE is 24.7%.<br />
<strong>Indirect</strong> RE (n=10’290)<br />
31
Figure A.9: Total household rebound effect<br />
Density<br />
0 5.204<br />
Median<br />
0 .2 .4 .6 .8 1 1.2 1.4 1.6 1.8 2 2.2 2.4<br />
Total microeconomic RE (n=10’290)<br />
Not:Note: <strong>The</strong> average total household rebound effect is 36.7%.<br />
32
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