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1 Study for the Directorate-General for Energy (DGXVII) of the Commission of the European Communities Final Report – May 1999 Energy Efficiency of Room Air-Conditioners (EERAC) Contract DGXVII4.1031/D/97.026 Co-ordinator: Jérôme ADNOT, ARMINES, France PARTICIPANTS Matthieu ORPHELIN, Cédric CARRETERO, Dominique MARCHIO Centre d’Energétique, Ecole des Mines de Paris, France Paul WAIDE PW Consulting, UK Michel CARRE Ademe, France Carlos LOPES CCE, Portugal Angel CEDIEL GALAN IDAE, Spain Mat SANTAMOURIS, KLITSIKAS University of Athens, Greece Bill MEBANE, Milena PRESUTTO, Enzo RUSCONI ENEA, Italy Herbert RITTER EVA, Austria Sule BECIRSPAHIC Eurovent Certification Dominique GIRAUD, Edgard BOSSOKEN INESTENE, France Luigi MELI, Stefano CASANDRINI CECED, Europe Philippe AUFFRET Electricité de France With the additional participation of other experts from EdF (France), ENEL (Italy), CECED and Eurovent Cecomaf (European manufacturers’ associations)

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Page 1: 5 Ecole Mines Paris EERACGB

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Study for the Directorate-General for Energy (DGXVII)

of the Commission of the European Communities

Final Report – May 1999

Energy Efficiencyof Room Air-Conditioners

(EERAC)

Contract DGXVII4.1031/D/97.026Co-ordinator: Jérôme ADNOT, ARMINES, France

PARTICIPANTS

Matthieu ORPHELIN, Cédric CARRETERO, Dominique MARCHIOCentre d’Energétique, Ecole des Mines de Paris, France

Paul WAIDEPW Consulting, UK

Michel CARREAdeme, France

Carlos LOPESCCE, Portugal

Angel CEDIEL GALANIDAE, Spain

Mat SANTAMOURIS, ���� KLITSIKASUniversity of Athens, Greece

Bill MEBANE, Milena PRESUTTO, Enzo RUSCONIENEA, Italy

Herbert RITTEREVA, Austria

Sule BECIRSPAHICEurovent Certification

Dominique GIRAUD, Edgard BOSSOKENINESTENE, France

Luigi MELI, Stefano CASANDRINICECED, Europe

Philippe AUFFRETElectricité de France

With the additional participation of other experts from EdF (France), ENEL (Italy),CECED and Eurovent Cecomaf (European manufacturers’ associations)

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CONTENTS

EXECUTIVE SUMMARY AND RECOMMENDATIONS ......................................................4

1. INTRODUCTION ...........................................................................................................12

2. ROOM AIR-CONDITIONERS IN EUROPE: TECHNICAL DEFINITIONS.....................14

2.1. Basic definitions....................................................................................................................................................... 14

2.2. RAC types ................................................................................................................................................................ 14

2.3. Test standards.......................................................................................................................................................... 18

2.4. RAC usage: a systems approach ............................................................................................................................ 19

2.5. Statistical databases, physical models created and information gathered.......................................................... 21

3. ROOM AIR-CONDITIONERS IN EUROPE ...................................................................23

3.1. European market for RACs in 1996 ...................................................................................................................... 23

3.2. EU production, imports and exports...................................................................................................................... 24

3.3. The stock of RACs in use in 1996 ........................................................................................................................... 25

3.4. Operation of the market.......................................................................................................................................... 26

4. ENERGY EFFICIENCY ON THE EUROPEAN MARKET..............................................30

4.1. Reference lines and models ..................................................................................................................................... 30

4.2. Previous market-transformation efforts within EU Member States................................................................... 32

4.3. The Eurovent Certification programme................................................................................................................ 33

4.4. The European Commission’s efforts to raise RAC energy efficiency ................................................................. 35

5. MARKET TRANSFORMATION OUTSIDE THE EU......................................................36

5.1. Minimum energy efficiency standards and labelling schemes in non-European countries............................... 36

5.2. Present situation in the USA................................................................................................................................... 36

5.3. Current schemes in Japan....................................................................................................................................... 39

5.4. The European market situation compared with other OECD countries ............................................................ 44

6. PROJECTIONS TO YEARS 2010 AND 2020 (BAU SCENARIO).................................46

6.1 Computation of energy consumption of appliances............................................................................................... 46

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6.2 Stock and market in 1990, 1996, 2010 and 2020 .................................................................................................... 49

6.3 Electricity consumption............................................................................................................................................ 52

6.4 – Environmental impact........................................................................................................................................... 55

7. TECHNICAL–ECONOMICAL STUDY OF OPTIONS....................................................58

7.2 Options and technical results................................................................................................................................... 59

7.3 Economic calculations for the screening of cost-effective measures..................................................................... 64

8. POLICY ACTIONS REALISABLE BY THE YEAR 2010 ...............................................70

8.2 Behavioural changes, controls, comfort conditions and thermal regulations...................................................... 75

8.3 Minimum energy efficiency standards.................................................................................................................... 76

8.5 Voluntary agreement of manufacturers, performance certification .................................................................... 84

8.6 – Actions by national bodies .................................................................................................................................... 86

8.7 – Summary of possible actions................................................................................................................................. 89

REFERENCES...................................................................................................................91

APPENDIX 1- INFORMATION ON REVERSIBLE AIR CONDITIONERS (EDF) ............93

Testing standards, terminology ..................................................................................................................................... 94

Technical analysis........................................................................................................................................................... 97

Technical/economic analysis .......................................................................................................................................... 99

Conclusions ................................................................................................................................................................... 101

APPENDIX 2 - ADDITIONAL STATEMENTS OF MANUFACTURERS’ ASSOCIATIONS.........................................................................................................................................102

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Energy Efficiencyof Room Air-Conditioners (EERAC)

EXECUTIVE SUMMARY AND RECOMMENDATIONS

Room air-conditioners (RACs) constitute a growing electrical end-use in the European Union (EU),yet the possibilities for improving their energy efficiency are not well known. RACs may be used inhouseholds and can be bought or ordered directly by their occupants and as such they can beclassified as domestic appliances. However, the same appliances are also commonly used in offices,hotels and small shops and therefore the impact of any policy measures proposed through this studyneeds to be explored for both the domestic and tertiary sectors on an almost equal basis.

The European Standard EN 814 specifies the terms, definitions and methods for the rating andperformance of air- and water-cooled air-conditioners. The standard energy efficiency index isthe ‘energy efficiency ratio’ (EER):

EER = Pc (cooling) / Pe (electrical)

Where Pc is the cooling capacity of the air conditioner in watts and Pe is the electrical input also inwatts. A similar index is used for reversible units to describe their performance in the heating modeand is conventionally called the ‘COP’ (coefficient of performance). To correspond to the Europeanindustry’s definitions, the following products categories have been used and either included orexcluded from the study:

Included in the RAC Excluded from the RAC

Single-packaged units Spot air-conditioners

Split-packaged units Dehumidifiers

Multi-split packaged units Close-control air-conditioners

Single-duct air-conditioners Control cabinet air-conditioners

Evaporative coolers

Desiccant coolers

The study makes use of two databases containing technical information on RAC models on themarket in 1997/1998. The origin of these data were the European manufacturers’ associationsEurovent and CECED. Data collected by Eurovent (multi-split, split, single-packaged and single-duct RACs) and by CECED (split and single-duct RACs) were merged for most of the analysesreported here and together represent about 80–90% of the models on the European market in1997/98.

Market and stock

Italy is the largest RAC consumer and the largest RAC manufacturer in the EU (accounting forabout half of all European production). RAC penetration is also higher in Italy than in other EUcountries. Greece, Spain and Portugal manufacture far fewer RACs than they purchase and henceare net RAC importers. France is a manufacturing country with a growing internal market. Germanyand Austria are experiencing market growth with increasing imports. The combined annual sales of

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RACs in the EU was about 1 600 000 units in 1996.

1996 Room air conditioner sales in the EU (Thousand units/year)

Country Split Multi-split Single-duct Single-packaged

Total sales Total stock inuse

Austria 10 000 6 040 3 000 4 760 23 800 79 000

France 99 750 29 000 38 250 11 000 177 000 1 259 100

Germany 65 000 19 500 90 000 20 000 19 4500 526 100

Greece 138 000 12 880 600 1 000 150 880 744 830

Italy 363 360 20 350 42 127 13 653 439 490 2 111 740

Spain 250 000 0 39 000 29 000 318 000 1 369 000

Portugal 35 600 7 400 900 1 900 45 800 322 820

UK 104 000 0 26 000 3 800 133 800 674 412

Others 39 000 11 700 54 000 12 000 116 700 315 660

EU 1 104 710 106 870 293 877 97 113 1 599 970 7 402 662

Market share 69% 7% 18% 6% 100% -

The total number of RACs installed in Europe is around 7 500 000 units, which is equivalent in sizeto the domestic market for one of the big US or Japanese manufacturers.

Energy efficiency

The distribution of RAC EERs about the average EER per type on the European market shows thatthere are makred differences in energy efficiency performance and a significant margin foroverall improvement

0

5

10

15

20

25

30

35

40

60

61-7

0

71-8

0

81-9

0

91-1

00

101-

110

111-

120

121-

130

131-

140

141-

150

151-

160

161-

170

EER/EERaver (%)

mod

els

(%)

Note that the present declared measurement tolerances are of the order of 6% in terms of the EER,that variable speed units are not accomodated by the test procedure and that some uncertaintiesabout practical test conditions remain for single-duct RACs. Following one of the studiesrecommendations, the Commission has prepared mandate M/274 to CEN, in order to improve theaccuracy and applicability of EN 814.

There have been some national RAC efficiency promotional programmes in the EU, such as EdF’s

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Promotelec programme in France, while in Portugal thermal regulations in construction have beendeveloped that specifically address air-conditioning. The European manufacturers’ associationEurovent has created a RAC performance certification programme called ‘Eurovent Certification’.A high percentage of the EU market is already included in the Eurovent scheme (some 99% ofthe EERAC combined database). The 10 most important European manufacturers are members ofthe scheme. However, thus far, single-duct units, a growing segment of the EU RAC market, havenot been included in the Eurovent Certification programme.

International situation

A number of RAC market-transformation initiatives have been implemented in regions outside theEU. The USA and some countries in Southeast Asia have had RAC energy labelling for manyyears. In Japan, quasi-mandatory voluntary minimum energy efficiency thresholds that excludethe sale of low-EER models are universally obeyed and are regularly reviewed and updated. Thetwo policy options of minimum energy efficiency standards (MEES) and energy labelling arejointly applied in many countries, including several developing countries, although not all. Animportant review of EER threshold values, energy labelling schemes and associated market-transformation impacts has been conducted for the current study, providing a sound basis for thedetermination of suitable values for future European legislation.

The principal conclusions of this comparative work are that there has been considerable legislativeactivity to improve air-conditioner efficiency around the world and that a large proportion of RACscurrently available for sale in the EU would not satisfy efficiency minimum efficiency thresholds inthe countries that have introduced such requirements – including those in many developingcountries. This suggests that there is significant scope to improve RAC energy performance in theEU and that to so does not require technological innovation, but merely implementation of well-established higher-efficiency design options. European or national efforts reported previously in thisreport appear very limited when compared to the schemes implemented in any of the countries orgroup of countries considered here.

Projections of energy consumption

An evaluation of air conditioner demand and usage patterns has enabled estimates of an equivalentnumber of hours of full-load air conditioner operation per year to be estimated by user sector andcountry. These were used to predict RAC energy consumption and to evaluate the cost effectivenessof the technical variations under investigation.

Estimated weighted-annual average hours of RAC usage by user sector in the EU

A base case, Business as Usual, scenario has been defined in order to analyse the technical andeconomic potential of single or combined policy measures in several alternative energy efficiencyscenarios. The year 2010 has been chosen for projection purposes in accordance with the deadlinefor the implementation of the Kyoto Protocol. Longer term porjections are given up to the year2020. The base year for the study has 1996 but backwards projections have been made to 1990 to beconsistent with the base year used under the terms of the Kyoto Protocol. Very conservativeoptions have been taken about future market growth, nonetheless the estimated growth forsome countries is still very rapid.

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Estimated RAC electricity consumption in the EU (GWh/year)

1990 1996 2010 2020

Austria 68.6 121.3 235.0 364.5

France 331.6 1 782.1 5 517.2 8 975.5

Germany 155.9 672.4 1 914.0 3 197.3

Greece 208.8 1 006.6 2 281.3 3 478.6

Italy 761.0 4 494.1 5 743.6 7 033.9

Portugal 162.4 713.8 1 806.8 2 552.2

Spain Not available 2 496.4 9 366.4 15 146.6

UK 120.0 446.0 1 135.7 1 783.8

Other EU 119.6 443.5 1 159.1 1 897.7

Total EU 1 927.9 12 176.2 29 159.1 44 430.2

Without policy intervention RAC associated CO2 emissions in the EU is conservatively projected toincrease by a factor of 11 from 1990 to 2010 (the timescales used in the Kyoto protocol) rising from1 million tonnes to 11 million. The projected increment in RAC related CO2 emissions is about 10M-tonnes (3000 M-tonnes being the initial CO2 emissions from all fuels in the EU). The directeffect of the growth of the RAC market on total EU emissions is therefore projected to be +0.33%without policy intervention, as compared with the -8% target for the EU as a whole.

Energy efficiency options

Among the seven RAC categories considered in this study, four specific models were selected closeto the centre of some representative ‘clusters’ for technical analysis: three very different models inthe largest category (splits = 69% of market) and one in a fast growing category (single ducts = 6%of the stock but 18% of the market).

Two types of questionnaires, one for air-cooled and one for water-cooled systems, were compiled inorder to collect the technical data and parameters needed to model the air conditioners underexamination. The questionnaires were submitted to the European room air conditionermanufacturers’ associations, which contacted the manufacturers of the selected representative unitsand asked them to provide the technical data to the study group. A room air conditioner energy-engineering simulation package was calibrated using the detailed technical data for each of the fourRAC models and then used to conduct simulations of a variety of known design modificationsleading to enhanced energy efficiency.

The full combination of options, using only proven design options, leads to a potential averageimprovement in performance of ~50%, part of which wouldn't be economic. The economic analysiswas performed estimating the net benefits of the technological options of the various models toconsumers. This needs a careful study of costs and overcosts and the use of criteria like Net PresentValue of investment or minimum of Life Cycle cost. In all cases, such as in the graph below, theleast life cycle cost is found to occur for a 25% performance improvement, corresponding to options(5+6+2b).

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BASE +25% +36% +48%

Policy options

The USA-LBL model for the appliance industry was used to evaluate the impact of this technicalscenario (+25% efficiency) on European manufacturers. With the rather low elasticity and thesubstantial benefits to consumers the unit shipments are predicted to increase, as much as 15% inthe combined case (5+6+2b options). This is the design option with 25% energy savings. Thepolicy option considered in the LBL model is quite strong (MEES at present average + 25%)and, despite the important advantages that would accrue, scenarios and policy options havebeen designed to give time and flexibility to the adjustment procedure.

It is recommended that municipalities, central administrations for southern EU Member States, etc.should introduce regulations or at least advisory schemes on RAC sizing and inside set temperaturesand should strongly promote the development of regionally specific energy consumptioncalculations. All the bases for the development of a common rule to easily compute RAC energyconsumption under local circumstances have been gathered in the present study. If an "installedappliance" scheme is proposed, all the required technical elements can be found in the present reportA significant energy saving potential exists from the development and improvement of RACmaintenance schemes. Terms of reference for such schemes could be defined with the nationalinstallers (and retailers) associations. How much of the 20% drop in RAC efficiency due to foulingcould be avoided by any given maintenance scheme and for a given cost is an interesting subject fornational evaluation, prior to or independently of any common European measure.

At EU level, the introduction of Minimum Energy Efficiency Standards is recommended withtwo sets of thresholds, one for enforcement before the year 2003, and another before 2010. Therecommended efficiency level of the second MEES is the present European market average EER +10%, which is still short (by 15%) of the cost effective optimum. Its impacts, obtained by a detailedstock simulation are given in the final table. The threshold values to be applied, in case they aredefined by types, are given hereunder.

Recommended minimum energy efficiency standards (MEES) for RACs in the EU (all values are for EERlevels (W/W))

Type of RAC First MEES(present marketaverage)

Current highest EERon the EU market

Second MEES(present marketaverage +10%)

MS,A: Multi-split, Air-cooled 2.63 3.74 2.89

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PA,A: Single-packaged, Air-cooled 2.38 2.97 2.62

PA,W: Single-packaged, Water-cooled 3.32 5.42 3.55

SD,A: Single-duct Air-cooled 1.80 3.09 2.28

SD,W: Single-duct, Water-cooled 2.36 3.62 2.60

SP,A: Split, Air-cooled 2.48 3.56 2.73

SP,W: Split, Water-cooled 2.75 2.88 3.03

A comparison has been made with the MEES and target thresholds applicable in the largest RACproducing countries. The proposed first and second MEES are just in the middle of the lines appliedby competitors up to 1998, but fall considerably short of the new efficiency targets in countries suchas Japan. The proposed MEES are clearly needed to avoid the outcome wherein the energyefficiency legislation enforced in a number of exporting South East Asian countries results ininefficient products that can no longer be sold locally being exported at discounted prices to the EU.

For energy labelling, four separate RAC categories could also be used for single-packaged units,splits, multi splits and single ducts. The EER measured according to EN 814 (at the T1 conditions)is generally representative of relative in situ energy consumption performance. Since the ‘unit’ EERvalue is not representative of the energy consumption for water-cooled systems, specific limitsshould be applied to their apparent EER. This leads to 7 RAC categories. The positive impact ofvariable speed technologies, such as 'inverters', or simply multispeed drives, that can be applied toany class of equipment, merits a positive correction for the nominal EER. Appraisal of this bonusshould be delayed; however, until the revision of EN814 provides more objective evidence on thesubject.

Potential energy labelling structure and thresholds: Air-cooled RACs

Label class limits EER/EERav Split Multi Split Packaged Single Duct

A starts over 150 3.72 3.95 3.57 3.11

B starts over 140 - 150 3.47 3.68 3.33 2.90

C starts over 130 - 140 3.22 3.42 3.09 2.69

D starts over 120 - 130 2.98 3.16 2.86 2.48

E starts over 110 - 120 2.73 2.89 2.62 2.28

F starts over 100 -110 2.48 2.63 2.38 2.07

G starts below 100 2.48 2.63 2.38 2.07

Potential energy labelling structure and thresholds: Water-cooled RACs

Label class limits EER/EERav Split Packaged Single Duct

A starts over 150 4.13 4.98 3.54

B starts over 140 - 150 3.85 4.65 3.30

C starts over 130 - 140 3.58 4.32 3.07

D starts over 120 - 130 3.30 3.98 2.83

E starts over 110 - 120 3.03 3.65 2.60

F starts over 100 -110 2.75 3.32 2.36

G starts below 100 2.75 3.32 2.36

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The models found on the market compare appropriately with this classification structure: no specificmanufacturer has problems and no product category is specifically prohibited from the higherlabelling classes. A model of the label has been prepared and its effect forecast. Note that a labellingstructure has also been produced wherein all the RAC categories are merged into one category. Thiscould be deemed to correspond more closely to the interests of the consumer (an A appliance havingalways the same performance level in absolute terms, whatever its porduct category) but it is notfavoured by some manufacturers.

C o o lin g o n ly / R ev e rs ib leA ir co o le d / W a te r co o led

S p litA /C

Ind ica tive ene rg y consum p tionkW h /(ye a r.m ²)A c tu a l e n e rg y co n su m p tio n w ill d e p e n d o nh o w the a p p lia n ce is u se d a n d o n c lim a te

C o o ling ca pac ity [kW ]

C o o lin g o n lyA ir co o le d

T ech n ica l g ro u p :S p lit, M u lti-sp lit, W indow ,S ing le -duc t

E n erg y co n su m p tio n :A verage nb o f hou rs * (100 W /m ²) /E E R

C o o lin g cap ac ity :a t T 1 cond itions

H ea tin g m o d e (o r n o t)C o o lin g m ed ia

A n y ce rty fy in g lo g oE uroven t o r o the r

The impact of the labelling scheme may increase after 2003, but labelling can also help the marketto adjust to the proposed MEES regimes. Nontheless, the impacts of the first MEES and of energylabelling combined are unlikely to be enough to make the market reach the economic optimum.Stronger actions, such as the second MEES and the involvement of manufacturers, national agenciesand utilities will be necessary to get closer to the optimum. These actions could bring the marketaverage EER in to the neighbourhood of the best models available today by 2020, 2015 or2010 depending on their vigour.

If voluntary agreements with manufacturers are proposed to obtain higher average EER levels, acertification scheme similar to the one existing for splits, multi splits and single-packaged unitsshould be introduced by the manufacturers themselves for single duct RACs. Targets for allsegments could be defined over the second MEES level, half way toward the economic optimum.

In terms of average performance, if the intention is to achieve the economic optimum (+25%) by theyear 2015 through a voluntary agreement, the WEER (Weighted EER) should change in thefollowing way.

Weighted EER corresponding to achieving the techno-economic optimum target by 2015 where the marketshares of the various RAC types used for overall averaging are their shares in 1996.

Year 1996 Check point

2000

Check point

2005

Check point2010

Target 2015

Splits (air) 2.48 2.79 3.10 3.10 3.10

Splits (water) 2.75 3.10 3.44 3.44 3.44

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Multi-splits 2.63 2.96 3.29 3.29 3.29

Packaged (water) 3.32 3.74 4.15 4.15 4.15

Packaged (air) 2.38 2.68 2.98 2.98 2.98

Single ducts (air) 2.07 2.33 2.59 2.59 2.59

Single ducts (water) 2.36 2.66 2.95 2.95 2.95

All RACs 2.44 2.75 3.06 3.06 3.06

One can judge the depth of a voluntary agreement by comparing the WEER reached with the WEERof the table above. Voluntary agreements may cover also some additional aspects such as advice onsizing, agreement to only offer high performance equipment to installers, indications of acousticpower on labels, etc…

All electric utilities and agencies can have an important role. Northern utilities can promote highefficiency reversible units; see annex 1. Southern utilities could support the European schemebecause of the savings it will induce in their investments

Aside from the +25% efficiency goal, what defines the target is the date at which this optimum isreached. The energy consumption and environmental impacts associated with various policy targetshave been estimated using the market stock model for the year 2010, the deadline for thesatisfaction of the Kyoto protocol targets and for the year 2020 and are summarised in Table 8.15.The average RAC life expectancy (10-13 years) and hence replacement rate is such that reaching thetarget in 2010 or 2015 requires almost immediate action, while targeting the year 2020 to reachtoday’s economic optimum would allows progressive measures.

Summary of targets and scenarios

Scenario Policy measures

(labelling is anaccompanyingmeasure in all cases)

TWhsavedper yearin 2010

TWhsavedper yearin 2020

CO2saved in2010 -% of19901

CO2saved in2020M-tonnes

Annualgain inManuf.Revenue(M-Euroin 2010)

Annualconsum-erbenefit(M-Euroin 2010)

Avoidedrisk in2020(southernutilities)

BAU No measure - - - - - - -

"First Step" 1st level MEES in2003 +labelling

0.6 1.6 60% 0.7 12 72 88

"Target2020"

MEES in 2003 and2007 +labelling

2.8 8.6 120% 3.4 57 336 411

"Target2015"

MEES in 2000 and2005 +labelling

3.3 9.4 100% 3.7 67 396 485

"Target2010"

2nd level MEES in2000 +labelling

4.4 10.3 140% 4 90 528 646

High energy savings are possible, as well as significant CO2 emissions reductions, at no (in factnegative) cost, such that all parties (manufacturers, consumers and utilities) would find a benefit inthe marketing of efficient RACs.

1 Around 1 Mt CO2 emitted in 1990 due to RAC on a total of fuel related emissions of 3000 MtCO2; the percentage isexpressed in the terms of the Kyoto protocol, i.e. related to the total 1990 emissions (like the 8% target), but only theRAC emissions. In terms of the total emission the values are between 0,02 and 0,07%.

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1. INTRODUCTIONSAVE II is an EU programme to promote the rational use of energy within the EU. The EERACworking group began a study in December 1997 to investigate the technical and economic potentialof measures to raise the energy efficiency of individual (or ‘room’) air-conditioners (RACs). Thisreport gives the final result of work to May 1999.

The objectives of the study were:

• to estimate the electricity consumption of RACs

• to estimate potential energy savings deriving from the use of more efficient RACs

• to investigate ways in which these savings can be realised, including behavioural changes andpolicy options (labelling, minimum efficiency standards, procurements, incentives, etc.)

• to make appropriate recommendations, on the basis of a cost–benefit analysis.

RACs can be used in households and are usually bought or ordered directly by the user. However,the same appliances are also frequently used for office and tertiary-sector building air-conditioning.As a result, the consequences of any measure need to be studied for both sectors on an equal basis.

The working party has been chaired directly by Paolo Bertoldi from DGXVII and co-ordinated byJérôme Adnot of Armines.

Choice of technical experts

• Armines is a research association supported by the Ecole des Mines de Paris and is especiallyactive in the field of energy efficiency, with activities ranging from technological developmentto socio-economic investigations.

• PW Consulting is a UK consultancy specialising in appliance energy-efficiency initiatives andprogrammes around the world.

• INESTENE is the leading consultancy on demand-side management (DSM) in France.

• Eurovent Certification is a creation of the Eurovent/Cecomaf manufacturers’ association for thecertification of the energetic and acoustic performance of air-conditioning and ventilationequipment.

• The University of Athens, in particular the Group of Building Environmental Studies, is veryactive in the field of solar cooling and energy conservation in buildings; the group carries outresearch, specialised studies, application projects, education, and dissemination of information.

Represention of Mediterranean countries

National representivity was increased with the participation of the following national agencies.

• Ademe, the French energy and environment agency.

• CCE, the Portuguese energy-conservation agency.

• ENEA, the Italian national agency for energy and the environment.

• EVA, the Austrian energy research and policy institution in which the federal and provincialadministrations (‘Bund’ and ‘Länder’, respectively) and some 30 important institutions andcorporations from a variety of economic sectors co-operate.

• IDAE, the Spanish energy-conservation agency.

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Direct representation of utilities

Utilities bring an important contribution and stimulation to the study of this growing end-use ofelectricity. Two were directly present:

• EdF (Electricité de France), the French electricity utility, represented by Hervé Rivoalean andPhilippe Auffret,

• ENEL, the Italian electricity utility, represented by Salvatore Russo and Alfredo Previ.

Close involvement of manufacturers’ associations

Two manufacturers’ associations are participating directly in the study. Not only have theyparticipated actively in the plenary meetings of the working party, but they have also held a numberof associated working meetings with their members (the manufacturers), including those at Roissy(February 1998), Milan (October 1997) and Rome (May 1998).

CECED is the European Council of Household Appliances, represented by its General Secretary,Luigi Meli, its Technical Secretary for energy performance, Stefano Casandrini, the Chairman of itsad hoc working group, Sergio Zanolin, and the Manager of its Italian branch, Antonio Guerrini.

Eurovent/Cecomaf is the manufacturers’ association for refrigeration, air-conditioning andventilation equipment, represented by its Director of Operations, Sule Becirspahic, the Chairman ofits group on RACs, Jan Cluyse, and one of its members, Ing Tavazzi.

Co-ordination was sought with the team that made previous efforts to prepare the application of the‘labelling’ Directive, namely that led by TNO of the Netherlands (TNO 19982). However, theobjectives of the current study differ from those of that previous study.

2 Common final report to contract nos. XVII/4.1031/Z/95-055 ‘Energy labelling of room air conditioners’ andXVII/4.1031/Z/96-024 ‘Energy labelling of domestic air to air heat pumps’, under the EC SAVE programme, alsofinancially supported by: NOVEM, the Dutch organisation for energy and environment, and NUTEK, the Swedishnational board for technical development.

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2. ROOM AIR-CONDITIONERS IN EUROPE: TECHNICAL DEFINITIONS 2.1. Basic definitions

The term ‘room air conditioner’ (RAC) is widely used in the USA and other English-speakingcountries and helps to distinguish these appliances from central (or ‘ducted’) air-conditioners. It isperhaps more precise to call RACs ‘individual’ or ‘autonomous’ air-conditioners, but the usual term‘room air-conditioner’ or ‘RAC’ is used in this study to avoid confusion. A ‘room air-conditioner’,as opposed to an ‘air-conditioning system’, is an appliance that can be bought by a household, witha direct link between the customer and the selection of the purchased good – either direct purchaseby the household or through an installer with whom negotiation and specification of the appliancetakes place.

On the other hand, ‘central air-conditioning systems’ have a central refrigerating unit and make useof a fluid to transport cold. They are specified by engineers or technicians, who define the systemassembly without the direct influence ofthe customer. They will not be considered in this study.

As illustrated in Figure 2.1, an RAC cools the room by ejecting heat outside of the room, eithercondensing some moisture or not.

Figure 2.1. Essential quantities in the process of room air-conditioning.

P c

P e

P r

T i

The terminology in this study corresponds to that used in the European test standard EN 814-1. Theappliance extracts heat from inside the room (Pc), leading to a lower temperature (Ti) through theuse of electricity (Pe). Usually the heat ejected outside (Pr) has an energetic value similar to Pe +Pc. The accepted energy performance index is called the ‘energy efficiency ratio’ (EER) and isdefined as:

EER = Pc / Pe

A similar index, the coefficient of performance (COP), is applied to indicate the performance ofreversible units in the heating mode.

2.2. RAC types

Air-cooled and water-cooled units must be included in the study. Evaporatively cooled units (whichare not frequently found within the study’s upper 12 kW cooling-capacity range) need not be treatedseparately in the study. Some single-duct units use a very limited volume of water for heatexchange. Note that these units are those that use water evaporation as the condenser heat-transfermedium, not evaporative cooling units (which evaporate water directly or indirectly in the processair). The few evaporatively cooled units are similar to air cooled units and will be assimilated withthem. On the other hand, the classic water-cooled units are a separate class: they use potable(drinkable) water to eject the heat, a fact that should not be forgotten in assessing theirenvironmental impact. The water used in an RAC could in principle be non-potable water, but this

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is seldom available.

For most of the available technologies, two types of operating mode are possible: cooling only andreverse cycle. The techno-economic assessment of reverse-cycle units in this study focuses on thecooling mode as it is the air-conditioning function that is the area of interest. None the less, somedata on the heating mode will be presented in an appendix.

Some systems have a variable refrigerant volume (by way of varying the compressor speed), whichresults in better part-load performance. They are called ‘inverters’ and will be studied as part oftechnical options.

As this study addresses air-conditioners that will be potentially used in the domestic sector, and asthe German market has many RACs using a 400 V, 3-phase supply but with a cooling capacity of5 kW, RACs with any input voltage will be included in the terms of the study.

Split-packaged units (split systems)

A split-packaged unit is defined as a factory assembly of components of a refrigeration system fixedon two or more mountings to form a matched functional unit. This type of appliance comprises twopackages (an indoor and outdoor unit) connected only by the pipe thattransfers the refrigerant. Theindoor unit includes the evaporator and a fan, while the outdoorunit has a compressor and acondenser.

Indoor units can be either fixed – whether mounted high on a wall (Figure 2.3), floor-mounted or as‘cassette’, ceiling-suspended, built-in horizontal or built-in vertical mountings – or, sometimes,mobile (Figure 2.4). The outdoor unit can be either fixed (see Figures 2.3 and 2.4) or mobile (Figure2.5). Whether the indoor or outdoor unit (or both) is mobile has no discernible influence on thesystem’s cooling capacity or energy performance. Ducted systems are a subclass among the splitsystems (Figure 2.6). These air-conditioners can deliver cool air to several rooms or to several spotswithin a single room; the smallest of these appliances currently have 7 kW of cooling capacity.Ducted systems are uncommon in Europe but are included in our study.

Multi-split-packaged units (multi-splits)

Multi-split-packaged units comprise several interior units connected to one exterior unit (Figure2.7). Multi-split systems will be investigated in the study, but there is a small problem in that manyconfigurations are possible (in terms of the number and type of indoor units that can be connected tothe outdoor unit). We shall consider here the maximum configuration, but the results can beextended as soon as EN 814 is extended.

Single-packaged units (window air-conditioners)

Single-packaged units, commonly known as ‘window’ or ‘wall’ RACs, are strictly defined as afactory assembly of components of a refrigeration system fixed on a common mounting to form asingle unit.

This type of equipment comprises a single package, one side of which is in contact with the outsideair for condensation, while the other side provides direct cooling to the inside air with a fan (Figure2.8). The two sides of the appliance are separated by a dividing wall, which is insulated to reduceheat transfer between the two sides.

This kind of unit often fits under or above a window or above a door. A distinction is generallymade between those units having louvered sides (designed to be installed in a window opening) andthose without louvered sides (designed to be installed in an opening in the exterior wall).

In general, window systems on the EU market are significantly less efficient than split systems;

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however, the ‘window’ market is small in Europe. According to some, they are less efficient partlybecause of their size but mostly because this is an old technology which has not been updated.

Single-duct units

These are appliances in which the condenser ejects hot air through a duct to the exterior (Figure2.9). They are generally movable, but in order to operate they must be set close to a window or adoor through which the duct eliminates the hot air. In principle, a dedicated hole should be made inthe envelope just for the appliance, as the use of doors and windows for the duct allows hot air toinfiltrate. There are difficulties in taking the thermal effect into account when measuring single-ductenergy performance. Furthermore, such penetration in the building envelope has an acoustic impact.

Other appliance types

Spot air-conditioners are comparable to single-duct RACs, except that the heat is directly ejectedfrom the back of the unit into the ambient air (if the window is closed, this appliance actually heatsthe room air while cooling the targeted ‘spot’). It is not a real air-conditioner.

Dehumidifiers are not included within the remit of EN 814. They do not permit temperature controland do not seem to have large market share, except in the UK. As a result they cannot be consideredas RACs and will be excluded from the current study. A further study would be required toinvestigate these appliances.

Neither evaporative nor desiccant cooling systems are directly studied in the EERAC project, butthey may be useful for comparison in Chapter 7. Evaporative cooling is an air-conditioning processin which the evaporation of water is used to decrease the dry-bulb temperature of the air. Somesmall appliances of this type are manufactured for the domestic sector (particularly in Greece). In adesiccant cooling system, the air is dried before being re-cooled by evaporative cooling (or a coolingcoil). This configuration is only used in industrial applications.

Evaporative and desiccant coolers are not really in direct competition with RACs. The market shareof evaporative cooling is small within the EU, and desiccant cooling is even less common.

Summary of appliances considered as room air-conditioners

Included in the RAC Excluded from the RAC

♦ Single-packaged units ♦ Spot air-conditioners

♦ Split-packaged units ♦ Dehumidifiers

♦ Multi-split-packaged units ♦ Close-control air-conditioners

♦ Single-duct air-conditioners ♦ Control cabinet air-conditioners

♦ Evaporative coolers

♦ Desiccant coolers

Only appliances of less than 12 kW cooling capacity are included in this study.

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Figure 2.3. Diagrammatic representation of a non-ducted fixed split-packaged unit.

Figure 2.4. Diagrammatic representation of a non-ducted split-packaged unit with mobile indoor unit.

Figure 2.5. Diagrammatic representation of a non-ducted split-packaged unit with mobile indoor andoutdoor units.

Figure 2.7. Diagrammatic representation of a multi-split-packaged unit.

Figure 2.6. Diagrammatic representation of a ductedsplit-packaged unit.

Figure 2.8. Diagrammatic representation of a single-packaged unit.

Figure 2.9. Diagrammatic representation of a single-duct air-conditioner.

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2.3. Test standards

Overview of international and national RAC test standards

European standards (EN) are called ‘CEN standards’ within the sense of the ISO/IEC definition of‘regional standards’ (Figure 2.2). Harmonised EU product testing standards are established by theEuropean agencies CEN and CENELEC, and Member States are obliged to implement themthrough their adoption as national standards.

Figure 2.2. Links between RAC test standards.

S tan dards on T esting and R ating

IS O 51 51 (1 994 )no n -d uc ted A C and H P

IS O 13 253 (1995 )du cted A C and H P

W O R L D S T A N D A R D S

R E G IO N A L S T A N D A R D S

E urop ean

E N 814 -1 ,2 ,3 (19 97 )A C and H P coo ling m ode

U S A

A N S I /A S H R A E16 -19 83 (1 983 )

R A C & P ackaged T e rm ina l R A C

Japan

J IS C 9612 (1994 )R A C

E N 255 -1 ,2 ,3 ,4 (19 97 )A C and H P hea ting m ode

A C = a ir co nd ition ing , H P = hea t pum p , R A C = roo m a ir co nd ition er

The full list of standards on performance, security and sound levels can be found in the references.For test procedures on acoustic (noise) testing, refer to Directive 86/594/EEC of 01/12/86 (OJL344,6.12.1986, P24). Some industrial testing conventions are found in Eurovent documents 6/6(Thermal Testing), 8/1 and 8/4 (Acoustic Testing), but these are not test standards in their own right.

Description of standard EN 814-1, 2, 3 (1997)

Within this standard:

• there is no restriction on voltage (i.e. 110, 220 and 340 V units are considered)

• there is no restriction on maximum cooling capacity

• ducted and non-ducted units are considered

• multi-split units are excluded

• continuously variable capacity control units are excluded.

The last restriction means that EN 814 excludes ‘inverter’-type RACs because it is difficult todesign comparative tests for inverter units: the energy performance of the inverters may be worsethan that of a ‘classic’ RAC at full load but can be appreciably better at part load. The existingstandards only define the tests at full load (maximum total cooling capacity at standard conditions).Single-duct appliances are covered by EN 814 but occurrences of their testing are still very limited.The exclusion of multi-splits is only because of the necessity of defining testing when only a subsetof the indoor units are connected, though in the meantime they can be tested with all the indoorunits connected. Work on these questions has been initiated in CEN following a mandate from theCommission.

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Basic principles of the EN 814 performance test

The EN 814 test standard defines many possible testing points, but normally only results recordedunder T1 and, in some cases, T2 test conditions are available (Table 2.1). Results may beappreciably different from one test condition to another as the TNO report has shown.

The EN 814 standard specifies that two test methods can be used: measurements can be performedeither using a calorimeter room or through an air-enthalpy method. The cooling capacity must bedetermined within a maximum uncertainty of ±5% independently of the individual causes ofmeasurement uncertainty. The electrical power must be measured within a maximum uncertainty of±1%. Thus, overall there is a permitted maximum uncertainty of ±6% in the measured EER.

A rating plate is fixed on each unit by its manufacturer to comply with the EN 814 standard. Therating plate contains at least the following information (in addition to compulsory informationrequired by safety standards):

• the manufacturer or supplier

• the manufacturer’s model designation and serial number

• the EER to two significant figures and the test condition (normally T1)

• the cooling capacity in kW, to one decimal place but not more than three significant figures.

Table 2.1. Test conditions under EN 814.

Rating Type of unit

Conditions Comfort air-conditioner orheat pump

Spot air-conditioner

Single-duct air-conditionera

Control cabinetair-conditioner

Close-controlair-conditioner

Air-cooled or air/air units

Mandatory test points

T1b A35(24)/

A27(19)

A35(24)/

A35(24)

A27(19)/

A27(19)

A35(24)/

A35(24)

A35(24)/

A24(17)

T2b A27(19)/

A21(15)

– – A50(30)/

A35(24)

Water-cooled or water/air units

Mandatory test points

T1 W30/A27(19) – – W15/A35(24) W30/A24(17)

Abbreviations: A = air; W = water.

Notes

a Single-duct discharges to outside air leaving the condenser: in order to maintain atmospheric pressure in test roomduring the test, outside air at 35 °C (24 °C) will be introduced and measured by pressure-equalising device ofcalorimeter.

b The wet-bulb temperature condition on the condenser is not required when testing units that do not evaporatecondensate.

2.4. RAC usage: a systems approach

Figure 2.10 describes the commercial, physical and legal operative framework of RACs. This kindof appliance is directly related to human comfort, or more precisely the absence of discomfort, andis influenced by local norms and building thermal standards. Actions on RACs interfere with other

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systems, such as heating in the case of reversible units, and with the environment.

Figure 2.10. Factors inflencing RAC use

loads

Utility

emissions

determination of national policies

RACcontrol

bill

local emissions+ heat

EuropeanPolicy

National Agencies

installer

merchant

demand

influence, support

manufacturer

Building Codes climate

Interior conditions

The conditions of comfort that are realised depend on the attributes of the RAC, as well as on thesubjective control of the user and on the building fabric. The price paid for electricity in the summeris certainly a factor influencing the appliance’s use. Climatic conditions differ greatly from one EUregion to another, as do indoor comfort expectations. Some of the need for cooling arises frombuildings’ solar gains and the heat transmitted through insulated walls. The amount of insulationused to minimise the need for heating also varies greatly between countries; and existing buildingcodes generate large differences in cooling requirements. The efforts of architects towards abioclimatic architecture, taking advantage of natural heat in winter and natural cool in summer, canbe very effective in some climates.

The so-called ‘single-duct’ appliances raise an important question from a systems perspective. Theyplay two roles: while cooling the air, they bring into the conditioned space air either from theoutside or from another room.

In addition to energetic performance information, RAC customers are also likely to be interested incomfort performance aspects such as acoustic comfort (noise levels) and dehumidification. It shouldalso be an option to indicate acoustic intensity on any RAC energy label because a low noise level isa highly desirable quality and is also positively correlated with RAC efficiency. None the less, adetailed study of acoustic comfort is obviously outside the scope of this study.

There is a range of ‘cooling needs’ in the residential sector, depending on users’ subjective feelings,values and decisions, that is much wider than the range of heating needs. Definitions of standardcomfort conditions for conditioned spaces are based on state-of-the-art knowledge; however, thelevels of discomfort that lead to the purchase of an air-conditioner have not been modelled. Thequality of air filtration provided by an RAC has been neglected during the modelling of theirdemand, as have RAC noise impacts and the avoidance of exposure to outside noise as a result ofbeing able to keep windows closed (except in the case of single-duct RACs, which may give rise toboth sources of noise in some cases).

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Interaction with some other energy policies

It can also be noted that public policies already have a large influence on the use of air-conditioning.Building codes relating to space heating have already been mentioned, but the increasing need forair-conditioning has been a concern for many national agencies responsible for saving electricity.Electricity utilities themselves may or may not welcome such increases in demand, depending onwhether they have summer or winter maximum power peaks and on their fuel mix.

Quality labels and promotional campaigns by manufacturers’ associations have already provedeffective. Specific sections of building codes in some countries, e.g. France and Portugal, deal withair-conditioning. Although they are frequently installed by professional fitters, RACs areincreasingly more mobile and can be installed by the end-user following their direct purchase. As aresult, the inclusion of RACs in the list of appliances under study at DGXVII was consistent with allthese efforts.

Local heat emissions of all kinds in Mediterranean cities in summer have already given rise to aheat-island effect, as in the southern USA, and the phenomenon has been measured in Athens. RACperformance can deteriorate greatly when local temperatures are higher than the normal regionalclimatic conditions, but this factor could not be taken into account in this study.

An important issue is whether or not the heating-mode energy performance of reversible unitsshould be taken into account in the overall evaluation of RAC energy performance. The studyauthors are in agreement with the following statement by TNO (1998): ‘In practice, reversibleappliances are distinctly marketed either as reversible air-conditioners or as reversible heat pumps.’As a result the study group believes it is more appropriate for the heating mode of reversible units tobe treated as an entirely separate issue from their cooling-mode performance. Air-conditionerperformance should be judged in the same manner regardless of whether the same appliance canalso operate as a heat pump.

Future studies will evaluate the gains attributable to reversibility. Information available in the publicdomain has been summarised in an appendix to this report.

2.5. Statistical databases, physical models created and information gathered

The conclusions of this study are based upon the information gathered from two technical databases,a number of computer models and national surveys performed in the countries that are directlyrepresented.

Technical databases

Two technical databases of models manufactured in 1997/98 were created using data originatingfrom two manufacturers’ associations, CECED and Eurovent. The CECED data are directlyreported by manufacturers and have not been independently verified. By contrast, the Eurovent datawere certified following the process described in section 4.2 and are published. CECEDmanufacturers and Eurovent manufacturers are not mutually exclusive sets since EuroventCertification works with all manufacturers ready to have their performance checked by outsideparties, including Eurovent/Cecomaf members as well as CECED members. The data collected byEurovent (on multi-split, split, packaged and single-duct RACs) and by CECED (split and single-duct RACs) cover 80–90% of the RACs of up to 12 kW cooling capacity on the European market in1997/98.

At the beginning of the study, RACs were distinguished according to their voltage (230 V and400 V), their mode of integration into the building and their differences in heat-transfer fluid (air orwater) and cycle type (cooling-only or reversible). This led initially to 19 RAC categories within the

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database, as shown in Table 2.2, though this number decreased as evidence was gathered.

Table 2.2. Classification and size of the RACs in the EERAC technical database

Category Description No. of models Percentage oftotal

MS1 Multi-split, 230 V, cooling-only, air-cooled 83 4.1

MS2 Multi-split, 230 V, reverse, air-cooled 49 2.4

S1 Split, 230 V, cooling-only, air-cooled 610 30.1

S2 Split, 230 V, reverse, air-cooled 543 26.8

S3 Split, 230 V, cooling-only, water-cooled 6 0.3

P1 Single-packaged, 230 V, cooling-only, air-cooled 32 1.6

P2 Single-packaged, 230 V, reverse, air-cooled 15 0.7

P3 Single-packaged, 230 V, cooling-only, water-cooled 68 3.4

P4 Single-packaged, 230 V, reverse, water-cooled 52 2.6

SD1 Single-duct, 230 V, cooling-only, air-cooled 58 2.9

SD2 Single-duct, 230 V, cooling-only, water-cooled 13 0.6

MS3 Multi-split, 400 V, cooling-only, air-cooled 20 1.0

MS4 Multi-split, 400 V, reverse, air-cooled 6 0.3

S4 Split, 400 V, cooling-only, air-cooled 228 11.2

S5 Split, 400 V, reverse, air-cooled 185 9.1

P5 Single-packaged, 400 V, cooling-only, air-cooled 15 0.7

P6 Single-packaged, 400 V, reverse, air-cooled 20 1.0

P7 Single-packaged, 400 V, cooling-only, water-cooled 18 0.9

P8 Single-packaged, 400 V, reverse, water-cooled 6 0.3

Total 2 027 100

The database contains statistics on more than 2 000 models on the European market. It isstatistically analysed later in this report (section 4).

National surveys

Separate national surveys have been conducted by members of the study group to provide additionalinformation such as:

• the historical evolution of the RAC market• the total number of RACs in use in 1996• the air-conditioned surface and the average rate of insulation in 1996• RAC trade marks, manufacturers and market shares• the different means of distribution and associated costs• the evolution of the equipment ratios of RACs• the potential of RAC sales as a percentage of available floor area or houses up until 2020• the U values of walls, and the comfort expectations of consumers• the generation fuel mix and customer tariffs.

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3. ROOM AIR-CONDITIONERS IN EUROPE 3.1. European market for RACs in 1996

The 1996 market share for each RAC type has been estimated firstly from the distribution of modelson the market in the technical database (assuming the market share is proportional to the number ofmodels available) (Table 3.1). Such figures will henceforth be called model-weighted figures.

Table 3.1. Number of models by RAC type in the EU in 1996.

RAC type Number %

Multi-split 158 7.8

Split 1 572 77.6

Packaged 226 11.1

Single-duct 71 3.5

Total 2 027 100

The 1996 EU RAC market has also been derived from national surveys of sales carried out for thisstudy, as summarised in Table 3.2. Such figures can be called sales-based figures.

Table 3.2. EU RAC market share by type in 1996, as determined in national surveys.

Country Total sales Split Multi-split Single-duct Single-packaged

Austria 23 800 10 000 6 040 3 000 4 760

France 177 000 99 750 29 000 38 250 11 000

Germany 194 500 65 000 19 500 90 000 20 000

Greece 150 880 138 000 12 880 600 1 000

Italy 439 490 363 360 20 350 42 127 13 653

Spain 318 000 250 000 0 39 000 29 000

Portugal 45 800 35 600 7 400 900 1 900

UKa 133 800 104 000 0 26 000 3 800

Othersa 116 700 39 000 11 700 54 000 12 000

EU 1 599 970 1 104 710 106 870 293 877 97 113

Market share 100% 69% 7% 18% 6%

a Estimated

From these two sources it is possible to compare the model-weighted estimate of the relative sales-weighted importance of the RAC categories on the European market with the sales-based estimate,as shown in Table 3.3.

Table 3.3. Model-weighted and sales-weighted estimates of EU market shares for each type ofRAC in 1996.

Model-weighted Sales-weighted

Multi-split packaged units 8% 7%

Split-packaged units 78% 69%

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Single-packaged units 11% 6%

Single-duct units 3% 18%

The two estimates diverge seriously only in the case of the single-duct RACs, which are known tobe under-represented in the database and which also probably have higher sales per model thanother types. The figures show that a good consideration of both split units and single-ducts isnecessary for adequate coverage of the European market, not just the split-unit segment.

3.2. EU production, imports and exports

As with other domestic appliances, a number of EU countries have specialised in the manufacture ofRACs, either because of the proximity of the market or because of their competitive advantage. Notall the figures are known, but it is likely that the trade is mostly intra-European. Europe maintains ahigh degree of self-sufficiency (some 70% of the market being produced locally, even if partlyexported), despite the relative smallness of its market in comparison with the USA and Japan.

Table 3.4 presents the number of units of RACs produced in some Member States. A decrease in themarket in 1993 affected Italian production. The number of units manufactured doubled between1993 and 1995.

Table 3.4. Number of units manufactured between 1992 and 1996.

Country 1992 1993 1994 1995 1996

France 124 480 137 050 150 900 176 100 182 300

Greece 10 000 12 000 17 000 21 300 20 500

Italy 344 550 311 448 386 674 564 146 459 867

These countries do not saturate the European market. A substantial flow of RACs is bought fromand sold outside the EU, as shown in Table 3.5. These figures are largely indicative becausecustoms statistics are not detailed enough to differentiate RACs from other air conditioningequipment.

Table 3.5 Comparison of RAC production, imports and exports by country in 1996 (thousands).

Country Market Domesticproduction

Imports fromEU countries

Imports fromnon-EU

countries

Exports to EUcountries

Exports to non-EU countries

Austria 24 0 23 7 6 0

France 177 182 40 32 47 30

Germany 195 123 30 45 3 0

Greece 151 20 106 25 0 0

Italy 439 460 60 242 183 140

Spain 318 127 25 166 0 0

Portugal 46 0 28 18 0 0

UK 134 60 22 52 0 0

Others 117 152 20 60 115 0

Total 1 601 1 124 354 647 354 170

Figures in italic are estimated values

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The main net exporters of RACs are Italy and France (Table 3.6).

Table 3.6. Number of RAC units exported from France and Italy between 1992 and 1996.

Country 1992 1993 1994 1995 1996

France 47 439 53 511 60 360 72 201 76 566

Italy 169 284 141 833 185 871 330 711 323 296

3.3. The stock of RACs in use in 1996

Based on the national surveys conducted in this study, the average life span of the four principalRAC types is as shown in Table 3.7. Experts indicate that replacement is largely due to the desirefor a new unit rather than equipment failure, due to good reliability and low annual usage.

Table 3.7. Average life span for each type of RAC.

Category Average life expectancy(years)

Split-packaged 12.6

Multi-split-packaged 12.6

Single-packaged 12.5

Single-duct 10.3

Given these sales figures and life spans, it was possible to calculate annual stock figures by country,as shown in Table 3.8.

Table 3.8. Stock of RACs in use by EU country from 1990 to 1996.

Country 1990 1991 1992 1993 1994 1995 1996

Austria 8 600 22 600 29 100 42 600 58 300 70 300 79 000

France 369 200 502 000 645 000 760 900 908 100 1 082 100 1 259 100

Germany 144 000 186 400 261 500 294 400 352 200 444 400 526 100

Greece 76 000 148 010 223 450 313 020 439 750 593 950 744 830

Italy 198 900 396 450 641 050 871 400 1 000 000 1 672 640 2 111 740

Spain n.a. n.a. 350 000 549 000 777 000 1 051 000 1 369 000

Portugal 136 670 159 900 199 250 230 210 261 400 295 930 322 820

UKa 153 112 222 612 290 212 354 312 431 612 540 612 674 412

Othersa 86 400 111 840 156 900 176 640 211 320 266 640 315 660

Total 1 172 882 1 749 812 2 796 462 3 592 482 4 439 682 6 017 572 7 402 662

a Estimates

Overall, Italian owners accounted for 28% of the total number (7.4 million) of room air-conditionersin use in the EU in 1996.

A breakdown of the figures showing the proportion of each of the four RAC types in use withineach country in 1996 is shown in Table 3.9.

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Table 3.9. Numbers of each type of RAC in use within each EU country in 1996.

Country Split Multi-split Single-packaged

Single-duct Total

Austria 33 400 21 300 16 600 7 700 79 000

France 752 000 183 850 106 500 216 750 1 259 100

Germany 198 600 59 600 74 500 193 400 526 100

Greece 138 000 51 830 555 000 * 744 830

Italy 1 504 697 90 177 134 860 382 006 2 111 740

Spain 972 000 * 245 000 152 000 1 369 000

Portugal 267 157 30 143 17 720 7 800 322 820

UK 516 790 * 54 867 107 755 674 412

Others 119 160 31 100 44 700 116 040 315 660

Total 4 501 734 468 000 1 249 747 1 183 451 7 402 662

Percentage oftotal stock

61% 6% 17% 16% 100%

* Included in the split-packaged units

The fraction of the stock comprising split RACs (61%) in 1996 is lower than that for newappliances on the market (69%), which confirms the continuing growth in the market share for thistype of unit at the expense of single-packaged ‘window’ units. The same applies to single-ductRACs (16% versus 18%).

3.4. Operation of the market

Both the present and future impact of RACs must be assessed globally and locally, because thevarious national electricity distribution utilities and the various customers have different needs.

RAC penetration by user sector

The number of households equipped with central air-conditioners is negligible in Europe, such thatRACs are the dominant system in households with electric air-conditioning (though these numberno more than 2% of all households). ‘Penetration’ is defined as the number of households with oneair-conditioner. Penetration rates in the EU show that domestic air-conditioning is far less commonthan in other industrial countries (e.g. 70% of households in Japan; 55% in the USA), although therate in the non-residential sector (offices, hotels etc.) is significantly higher, since differentconstruction techniques are used and different levels of comfort are required.

Main trade marks

The total European market is equivalent in size to the domestic market of just one of the big US orJapanese manufacturers. Japan alone has an internal market of 8 million units per year, 5 times thesize of the EU market!

According to the information gathered for this study, it appears that about 10 manufacturers operateon an EU-wide level. This is not a result of large-scale production but reflects the fact that a numberof countries have a significant market and that there is a transfer of technology from countries with alarge market (e.g. Japan, the USA) to their European branches. Of the big 10 manufacturersmentioned, at least seven conform to this pattern. This does not mean that the local companies haveno technical autonomy, but it does explain the structure of the market.

The 10 main trade marks have been ranked in order of market share, as estimated from national

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market-share data (Table 3.10). They have been determined from the sum of the total number ofRACs sold under each trade mark in each of the five countries (Greece, France, Italy, Spain andPortugal) for which data were available. The ‘100%’ shown in the table in fact represents 62% ofthe national markets of these five countries, the total number of RACs sold across all brands being1 131 171.

Table 3.10. Dominance of main trade marks sold in Greece, France, Italy, Spain and Portugal (1996).

TRADE MARKS Number of

RACs sold in 1996

Percentage among

top 10

A 146 900 20.8

B 108 905 15.4

C 97 737 13.9

D 74 229 10.5

E 62 790 8.9

F 60 420 8.6

G 41 680 5.9

H 40 314 5.7

I 38 644 5.5

J 33 425 4.7

Total 705 044 100%

The 23 other trade marks specifically mentioned in the surveys sold a total of 320 154 units in 1996in these five countries.

Distribution structure and customer demand

One factor determining RAC distribution by type is the increasing ease of installation and use.‘Window’ units and multi-splits still require a fitter. Splits and, increasingly, single-ducts arebecoming more widely available in department stores and DIY retailers. Splits are becoming partlymovable in response to customer demand.

The domestic market for RACs is considered to be an ‘impulse’ market. This is true even if theRAC is installed professionally. The growing proportion of directly purchased RACs leads logicallyto an increase in the number of single-duct units discharging through partly opened windows,despite manufacturers’ recommendations. The volume of RAC sales correlates with outdoortemperature ( if there is a long period of hot weather, i.e. more than two weeks, sales figuresincrease rapidly).

Multi-split units are distributed and installed by heating and cooling plumbers because theirinstallation usually requires specialised knowledge of air-conditioning and ventilation technologies.In northern European countries, almost all window RACs are distributed by heating and coolingplumbers and electricians, while in some southern Member States they are also available directlyfrom shops.

As in other parts of the world, room air-conditioning in Europe is needed particularly in buildings ofpoor quality. Over the last few years, increasing numbers of lofts in old houses have been convertedinto flats in order to gain new living space. These flats can become very hot in summer and must becooled, especially when they are badly insulated. The costs associated with professional installation

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are not negligible. We have estimated installation costs for split systems, the dominant segment ofthe market, in various EU countries and these range from 15% to 30% of the purchase price.

Since not all appliances are installed by a professional installer, the most important piece ofinformation that is widely available (the nominal EER) should be attached to the appliance ratherthan be given only to the installer. It is true that the thermal quality of the building has a veryimportant impact (as important as the nominal EER) on the amount of electricity consumed by anRAC.

Past market evolution

It is important to consider recent growth trends in the RAC market (Figure 3.1).

Figure 3.1. Total sales of RACs in the EU in recent years (1990 - 1996).

EVOLUTION OF TOTAL RAC SALES

0

200000

400000

600000

800000

1000000

1200000

1400000

1600000

1990 1991 1992 1993 1994 1995 1996

Other E.U*

U.K

PORTUGAL

SPAIN

ITALY

GREECE

GERMANY

FRANCE

AUSTRIA

Figure 3.1 reveals a significant decrease in sales of all RACs in 1993, regardless of the type of unit.In particular, total sales in Spain declined by 42% from 1992 to 1993. A less marked declineoccurred in other countries during the same period, with annual sales decreases of between 5% and10%. This major sales dip could have resulted from the economic recession of 1993, with an overallreduction in the purchase of ‘comfort appliances’, together with a cooler summer than in 1994 and1995.

Evolution of the southern European market

In order to explore the possible impact of various policy measures, detailed country-by-countryforecasts of the EU RAC market to the year 2020 will be made and will take into account theincrease in the number of households (population change, change in household size) and incommercial customers and the increase in RAC penetration rate (ownership levels).

In fact, in some cases the same analysis may be performed by climatic zone for the reasonsdiscussed in section 2.4. For example, construction techniques and climatic conditions in Spain,

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which is a large potential market, mean that there are three distinct areas with differing RACpenetration rates, which should be treated separately: the north coast, like Portugal, will always havelimited penetration; the interior plateau, with its continental climate, is likely to experience highgrowth; while the Mediterranean coast is between the two.

The Italian market is showing the first signs of saturation, but it still has further growth potentialowing to transfer from the lowest segment of the market to the higher. In Portugal, meanwhile,according to estimates from CCE and the manufacturers’ association, the number of RACs soldthere will increase by a factor of five within 24 years. According to recent market studies performedby IDAE, Spain has a high potential for RAC sales growth, with more than 5 million householdshaving thermal and climatic characteristics that may generate a demand for this kind of equipment.Moreover, manufacturers are of the opinion that the Spanish market will double in the next 10years, after which it will stabilise. The forecast annual growth rates are 1% for Italy and 7% for themost promising countries: Greece, Portugal and Spain.

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4. ENERGY EFFICIENCY ON THE EUROPEAN MARKET 4.1. Reference lines and models

RAC performance distributions

As an initial step, the empirical distribution of the EER (energy-efficiency ratio) was studied for the19 categories defined in section 2.5 and for the total market (Figure 4.1).

RAC energy performance by category

The percentage difference between the maximum (or minimum) EER and the average (EERaver) isshown for each RAC category in Figure 4.2.

Figure 4.1. Distribution of EER/EERaver for allRACs on the EU market (1996).

0

5

10

15

20

25

30

35

40

60

61

-70

71

-80

81

-90

91

-10

0

10

1-1

10

11

1-1

20

12

1-1

30

13

1-1

40

14

1-1

50

15

1-1

60

16

1-1

70

EER/EERaver (%)

mod

els

(%)

Figure 4.2. Distribution of EER/EERaver per type

Average nominal EER values for each category are given in Table 4.1.

Table 4.1. Minimum, average and maximum performance on the European market

RAC category Cycle type Heat transfer EER

230V mono-phase cooling mode fluid min ave Max

MULTI-SPLIT Cooling only Air 1.91 2.70 3.74

Reverse Air 2.08 2.53 2.94

Air 1.54 2.53 3.56

SPLIT Cooling only Water 2.70 2.75 2.88

Reverse Air 1.45 2.48 3.45

Air 1.88 2.38 2.77

PACKAGED Cooling only Water 2.11 3.32 5.42

Air 1.93 2.32 2.84

Reverse Water 2.26 3.20 5.31

Air 1.35 2.07 3.09

SINGLE-DUCT Cooling only Water 2.10 2.33 3.62

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400V three-phase cooling mode Fluid min ave max

MULTI-SPLIT Cooling only Air 1.91 2.66 3.32

Reverse Air 2.10 2.34 2.55

Cooling only Air 1.59 2.40 3.25

SPLIT Reverse Air 1.70 2.46 3.20

Air 1.79 2.38 2.97

PACKAGED Cooling only Water 3.08 3.55 4.39

Air 1.79 2.44 2.97

Reverse Water 2.42 3.67 4.33

a Including some certified values and some manufacturer-reported values; values for single-duct RACs include specificuncertainties, as discussed in section 2.6.

Within each general category the water-cooled systems have systematically higher EERs, but thewater consumption is not negligible. The lowest EER values are found in the SD (single-duct)category. In most cases (except in three categories that are almost non-existent on the market:PA/E/Wt, MS/R/At, SP/C/A, see figure 4.2), the user will find high-performing and poorlyperforming models in any one category.

However, if the total range of performance is large, it should be said that most models concentratearound the average. Some 66% of the RACs in the database are in the range of 90–110% of theaverage EER. Some 90% are in the range of 80–120% of the average EER. It seems that only asmall percentage of appliances are either very efficient (4%) or very inefficient (6%).

Dependence of EER performance on cooling capacity – reference lines

Linear regressions of the EER against cooling capacity (the only performance parameter currentlymade available to purchasers) were computed for each RAC category (one of which is shown inFigure 4.3). The results, which produced more or less flat regressions, showed that there was nosignificant relationship between RAC EER and cooling capacity. The reference lines that can bedefined in terms of cooling capacity can only be horizontal lines.

Figure 4.3. EER vs cooling capacity (split, 230 V, cooling-only, air-cooled air-conditioners)

0

1

2

3

4

5

6

7

0 2 4 6 8 10 12

Total cooling capacity - Pc (kW)

EE

R (

Pc/

Pe)

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Cluster theory and the selection of reference models

For reasons of economy the techno-economic analysis requires the identification of some base-caseRACs to represent the typical design and cost-performance characteristics of an entire class of air-conditioners. The following four steps have been implemented to identify such base-case models inthis study:

• definition of RAC categories (see section 2.3)

• statistical clustering inside categories (for large ones)

• whenever possible, elimination of redundant clusters or categories (e.g. if there are too fewmodels in the given cluster for it to be statistically representative)

• selection of representative models in the remaining clusters.

The process first entailed the selection of the 10 most significant of the 19 RAC categories,followed by the identification of 20 different clusters. Since cluster theory is comparatively new, thegeneral principles are reviewed later. Its application has only been appropriate in this case becausethe available data are of a high quality, which is not always the case in market studies. These dataallowed the focused technical study which is reported in Chapter 7.

Noise levels

It should be mentioned that testing of RAC noise levels shows that there is an enormous range inacoustic performance though there is a clear relationship with cooling capacity, i.e. smaller RACsare generally far quieter.

4.2. Previous market-transformation efforts within EU Member States

Utilities such as EdF (France) and ENEL (Italy), national energy agencies, ministries, consumerassociations etc. have in the past made attempts to advise the wider public about better equipmenton the market in order to help manufacturers promote energy efficiency, for instance. As an exampleof these local or national efforts, which until now have been temporary and not coordinated acrossthe unified market, one of the most ambitious campaigns, currently under way, is the ‘EdF directoryof energy-efficient reversible air-conditioners’, discussed here.

An example of a utility-led energy-efficient RAC promotional campaign

EdF aims to promote reversible air-conditioners as the principal heating source in new Frenchhouseholds and is directing its promotional efforts in the following ways:

• the branding of some global commercial offers (not just the appliances) by EdF under the nameof PROMOTELEC, which also serves to promote some non-competitive electricity uses

• the provision of financial incentives under the VIVRELEC campaign to thousands of newhouses if they attain thermal performance levels that exceed the current mandatory buildingregulation levels (which are expected to remain stable)

• the affiliation of reversible air-conditioner manufacturers with the business association GIEClimatisation et Développement, which carries out collective advertising aimed at RAC marketdevelopment, in exchange for which affiliates sign a formal agreement with EdF to submitproducts for inclusion in EdF’s new ‘directory’

• the establishment and promotion of the ‘EdF directory of energy-efficient reversible air-conditioners’ (available from February 1999), which will indicate the appliances on the market

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that are efficient enough to be used in the PROMOTELEC/VIVRELEC schemes previouslydescribed.

Participating manufacturers must supply Eurovent with more test-point data than the minimumrequired to enter Eurovent (which are currently the T3 test results in the heating mode and the T1test results in the air-conditioning mode). Supplying this data to Eurovent means that it can beindependently verified. EdF also obliges products promoted within the directory to attain aminimum energy efficiency value under each test condition, as defined in Table 4.3. All values usedare Eurovent certified values, subject to independent testing.

Table 4.3. Threshold energy performance values for inclusion of RACs in the ‘EdF directory of energy-efficient reversible air-conditioners’.

Mode External unit Internal unit Minimum COP

Dry-bulbtemperature

(°C)

Wet-bulbtemperature

(°C)

Dry-bulbtemperature

(°C)

Wet-bulbtemperature

(°C)

or EER

Cooling mode 27 19 35 24 2.4

Heating mode 7 6 20 12 2.7

–7 –8 20 12 1.6

Abbreviations: COP = coefficient of performance; EER = energy efficiency ratio.

The management of the scheme will be conducted by Eurovent Certification, so that the Frenchdirectory of energy-efficient products will coexist with the European directory of certified products.The testing expenses will be covered by the manufacturers wanting to enter the scheme, and themanagement costs will be covered by EdF. The new directory will be used by the PROMOTELECfield promoters to advise customers about existing efficient models.

Compared with previous temporary national initiatives, the establishment of a permanent Europeanframework is likely to be more durable and could take advantage of the existing public familiaritywith the A–G energy efficiency ratings currently used to label a number of other types of appliance.

An example of a national scheme to promote energy-efficient RACs through building thermalregulations

As described in section 2.4, thermal insulation, which is often introduced into building codes tolimit heating requirements, very often has a positive influence on cooling needs; however, in othercases increased insulation could create summer discomfort and lead to the purchase of a newappliance.

European national building codes usually deal only with winter energy consumption and are notintended to influence energy consumed in room air-conditioning. It appears that only Portugal hasan alternative approach, that of imposing limiting values on both summer and winter energy needs.The idea is that the building code will result directly in reduction of energy consumption in summerand indirectly through a reduced need for appliance installation because of acceptable comfortlevels. Furthermore, the regulations require the installation of a central system when the coolingload is above 25 kW.

4.3. The Eurovent Certification programme

A transnational performance-certification programme is managed by Eurovent Certification, which

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is a business association created for this purpose, not a notified body. Equipment with EuroventCertification has been selected independently (not by the manufacturer) and then tested according tointernational standards in a replicable way (the same testing equipment is used for all testedappliances). Models to be tested are selected randomly by Eurovent. Specific units are pickeddirectly from the production lines. Though testing is conducted independently of the manufacturers,they have to cover the expenses of both the management of the programme and the testing.

Organisation of the programme

The objective of participating manufacturers is to have their appliances’ performance tested andreported in the annual directory, which is circulated to around 20 000 consultants and installers, andto be allowed to use the Eurovent label (Figure 4.4). For a cost of less than 0.2 % of their totalproduction costs manufacturers can, depending on the number of models, have all their modelslisted in the directory.

About 10% of all models on the European market are actually tested every year. The fear of a testresult that contradicts their own information has led a number of manufacturers to readjust theindication of EER in their commercial documentation. It should be noted that the values claimed inthe participants’ literature should not differ from the actual Eurovent laboratory test results by morethan 8% on the EER (combining error in measurement and error in sampling).

Effectively, errors are in fact lower than this value. The average margins of error are 5% in coolingcapacity and 1% in electrical capacity, giving a possible total margin of about 6% on the EER.Combined with a measurement error of the same order of magnitude, this could mean in an extremesituation a 12% error margin, rather more than the accepted allowable error of 8% and much higherthan what is generally found. In practice, when data from various laboratories are examined, thedifferences are found to be less than 3% for cooling capacity and 1% for power input. This couldmean an effective 4% error margin on the values stated in the catalogue (far less than the values justreported under the standard).

Marking of appliances

With this definition of acceptable errors, one can rely on the values given in the Eurovent directoryfor studying the european market. The equipment tested in that way and included in the directory ismarked with the following label:

Figure 4.4 Label stamped on Eurovent certified appliances.

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A high percentage of the European RAC market is already included in the Eurovent scheme (forinstance, 99% of our database, and probably 80-90% of the total market). The 10 most importantmanufacturers listed in section 3.5 all participate in the scheme. At present single-duct units havenot been included in the Eurovent Certification programme.

4.4. The European Commission’s efforts to raise RAC energy efficiency

The Directive on Efficient Appliances defines a framework for policy actions. The EuropeanCommission may combine these informative measures with other measures such as minimumperformance values and voluntary agreements to accelerate the penetration rate of more efficientappliances.

The rating system (using letters A–G) already used to label other types of appliance has proved to beeducational and may be appropriate for RACs. The commitment of CECED, the dominantassociation in the area of household appliances, has increased the impact of these measures. Underthis E&E umbrella, specific voluntary agreements have been signed with the Commission. No suchresult has been obtained yet for RACs.

A contract was awarded to TNO (the Netherlands) (Contract SAVE no. XVII/4.1031/Z/95-055) on‘Energy labelling of room air-conditioners’, the results of which have been available for the currentstudy. The TNO study team proposed to compare every single appliance’s EER, as certified byEurovent, with the average EER for all Eurovent appliances in the same category.

Meanwhile, as a partial result of the present study, the Commission has sent a mandate to CEN inorder to improve the accuracy of EN 814, particularly with respect to cooling capacity and otherspecific RAC features. In particular, the aim is to identify measurement methods that:

• cover all existing types of RACs

• allow for testing at full and partial loads

• allow for testing in a number of different climatic conditions

• consider reversible function (heating mode)

• develop adequate measurement methods for single-duct units

• improve accuracy and replicability for small-capacity equipment.

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5. MARKET TRANSFORMATION OUTSIDE THE EU 5.1. Minimum energy efficiency standards and labelling schemes in non-Europeancountries

Table 5.1 summarises known energy-performance test protocols, mandatory and voluntary energy-rating labelling programmes, minimum efficiency standards and voluntary agreements applicable toRACs in various countries around the world as well as the EU. Detailed reports have been made oneach. The applicable testing standards in these countries have been reviewed as well, and theseindicate a high degree of convergence with the relevant ISO standards (the parent standards ofEN 814).

Table 5.1. RAC energy-performance programmes around the world.

Country Energy Energy label Minimum efficiency standards

protocol Mandatory Voluntary Mandatory Voluntary

Australia Yesa Yes No No

a No

Canada Yes Yes No Yes No

China Yes No Noa

Yesa No

Taiwan Yes No No Yes No

EU Yesa

Noa

Noa

Noa

Noa

Hong Kong Yes Noa Yes No No

Indonesia Yes Noa

Noa No No

Israel Yes Noa No No No

Japan Yesa

Yesa No No Yes

Mexico Yes Yes No Yes No

New Zealand Yesa

Noa Yes No

a No

Philippines Yes Yes No Yes No

Russia Yes No No Yes No

South Korea Yesa Yes No Yes Yes

Thailand Yesa

Noa Yes No

a No

USA Yes Yes Yes Yes No

a Under review.

5.2. Present situation in the USA

Minimum efficiency standards in the USA

Under the terms of the 1987 National Appliance Energy Conservation Act (NAECA) the USAintroduced mandatory minimum energy efficiency standards (MEES) for RACs which becameeffective on 1 January 1990. These were followed by MEES for central air-conditioners in 1992 andfor split and single-packaged systems in 1993.

In 1994 the US Department of Energy (USDOE) proposed a revised standard for RACs based on a

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fresh techno-economic analysis. This was circulated for stakeholder review and eventually led to anagreement being reached between industry and energy-efficiency advocates for the next round ofstandards. The new standards were published in October 1997 and will enter into force on 1 January2000 (Table 5.2). The new standards not only include tougher energy efficiency ratio thresholds buthave added a new RAC category for units installed in casement windows (narrow windows openingon vertical hinges). The USDOE is currently reappraising the existing standards for central air-conditioner units.3

Table 5.2. US minimum energy efficiency standards for RACs, defined in 1997 and applicable from 1 January2000.4

Product class and cooling capacity (Btu/h) [kW] EER (Btu/Wh) [W/W]

Without reverse cycle and with louvered sides

<6 000 [1.76 kW]

6 000–7 999 [1.76–2.34 kW]

8 000–13 999 [2.34–4.10 kW]

14 000–19 999 [4.10–5.86 kW]

>20 000 [5.86 kW]

Without reverse cycle and without louvered sides

<6 000 [1.76 kW]

6 000–7 999 [1.76–2.34 kW]

8 000–13 999 [2.34–4.10 kW]

14 000–19 999 [4.10–5.86 kW]

>20 000 [5.86 kW]

With reverse cycle and with louvered sides

<20 000 [5.86 kW]

≥20 000 [5.86 kW]

With reverse cycle and without louvered sides

<14 000 [4.10 kW]

≥14 000 [4.10 kW]

Casement-window air-conditioners

Casement onlya

Casement slidera

9.7 [2.84]

9.7 [2.84]

9.8 [2.87]

9.7 [2.84]

8.5 [2.49]

9.0 [2.64]

9.0 [2.64]

8.5 [2.49]

8.5 [2.49]

8.5 [2.49]

9.0 [2.64]

8.5 [2.49]

8.5 [2.49]

8.0 [2.34]

8.7 [2.55]

9.5 [2.78]

a Casement only and casement-slider RACs were not treated as separate product classes for the 1990 minimum energyefficiency standards (MEES), but were subject to the MEES according to their cooling capacity and absence or presenceof louvered sides and a reverse cycle.

Energy labelling in the USA

Mandatory RAC energy labelling has been in place in the USA since 1975 and is the responsibilityof the Federal Trade Commission. The current US label, the ‘Energyguide’, is shown in Figure 5.1.

3 Turiel I. ‘Present status of residential appliance energy efficiency standards – an international review.’ Energy andBuildings 1997; 26 (1). 4 10 CFR Part 430: Energy conservation program for consumer products; conservation standards for room airconditioners; final rule, Department of Energy, Office of Energy Efficiency and Renewable Energy, 24 September1997.

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It uses a horizontal sliding scale to rank comparative RAC energy efficiency that ranges from ‘leastefficient model’ to ‘most efficient model’. The air-conditioner EER is highlighted in the centre ofthe label in large numbers and is expressed as British thermal units per hour (Btu/h) of coolingcapacity divided by electric power input in watts. Unlike most other labelling schemes, the older USlabel does not use a graded rating approach. The label sought to avoid generalisation by providingrunning-cost information under all usage and tariff situations, but this is very complex for theaverage consumer to assess. Indication of the EER also requires consumers to understand that a highvalue is more energy-efficient, something that may not be immediately evident. The US heat pumpEnergyguide label is similar in principle to the RAC label.

Figure 5.1. The US RAC energy label.

In addition to mandatory comparative energy labelling of RACs and heat pumps, the USEnvironmental Protection Agency (EPA) has introduced its ‘Energy Star’ voluntary award-styleenergy label for central air-conditioners and heat pumps that meet minimum performance criteria(Figure 5.2). To be eligible to receive the Energy Star label, central air-conditioners must have anEER of 12 or more (compared with the MEES EER requirement of 10). The aim of the Energy Starlabel is to provide additional market pull for the more efficient products on the market and toencourage manufacturers to market products that exceed the basic MEES requirements. Central air-conditioners with EERs as high as 13 to 16 are reportedly found on the US market.

Figure 5.2. The US Energy Star label applicable to central air-conditioners and heat pumps.

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Impact of MEES and labelling on the US RAC market

Between 1973 and 1993 the efficiency of US RACs improved by 51% and their energy consumptionunder identical operating conditions fell by 34%.5 The USDOE estimates that the new MEES due tocome into force from 1 January 2000 will raise the average cost of an RAC by ~$US10–20 incomparison with existing models but that the energy savings over the model’s lifetime will typicallybe between 2 and 6 times the incremental cost. The USDOE estimates that these revised MEES willproduce savings of ~$US270 million in consumer electricity bills by 2010 as a result of an averageimprovement in RAC efficiency of ~10% compared with 1997 levels.

Figure 5.3. Shipment-weighted average energy-performance trends for RACs in the USA.

0

100

200

300

400

500

600

700

800

900

1000

1972

1973

1974

1975

1976

1977

1978

1979

1980

1981

1982

1983

1984

1985

1986

1987

1988

1989

1990

1991

1992

1993

1994

1995

1996

Uni

t ene

rgy

cons

umpt

ion

(kW

h/ye

ar)

0.0

0.5

1.0

1.5

2.0

2.5

3.0

EE

R (

W/W

)

Energy consumption (532.5 hours/year)

EER

Figure 5.3 shows the evolution of the shipment-weighted average RAC energy consumption andEER over the same period in the USA. By 1996 the sales-weighted average EER of a US RAC(excluding split systems) was 2.66 under the equivalent of the ISO 5151 T1 test condition.

5.3. Current schemes in Japan

In 1979 Japan introduced its Law Concerning the Rational Use of Energy that set minimum energyefficiency targets for household air-conditioners applicable to producers and importers. At that timethere were no reversible units (heat pumps), so the targets only applied to the cooling mode. Targets

5 McInerney EJ, Anderson V. ‘Appliance manufacturers’ perspective on energy standards.’ Energy and Buildings 1997;26 (1).

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for heat-pump air-conditioners (reversible units) were added in 1994, and the cooling-only targetswere revised. Both the new and 1979 targets are voluntary in that there is neither formalenforcement nor legal penalties for non-compliance; however, the risk of public humiliation througha government announcement of manufacturer non-compliance is taken seriously in Japan andtherefore compliance is believed to be universal. The target values are shipment-weighted averagesand thus are somewhat weaker than a mandatory minimum-efficiency threshold set at the samevalue. In March 1999, the Ministry of International Trade and Industry (MITI) announced asubstantial toughening of the RAC energy efficiency thresholds as part of their Top Runner energyefficiency strategy aimed at fulfilling Japan’s obligations under the Kyoto protocol. The newlyannounced standards are the toughest in place globally.

Air-conditioner efficiency trends in Japan prior to 1994

The average efficiency of typical Japanese cooling-only RACs increased by 40.7% between 1973and 1979, although much of this improvement has been attributed to the fact that manufacturersknew efficiency regulations were likely to be drafted.6 From 1979 to 1983, the year when targetshad to be met, average efficiency improved by a further 20.2%, but from 1983 to 1993 it improvedby only a further 6.0% (Figure 5.4).

Figure 5.4. Trends in average Japanese air-conditioner performance (cooling-only, for units of 1 600 kcal/hcooling capacity).

0

100

200

300

400

500

600

700

800

900

1973 1975 1977 1979 1981 1983 1985 1987 1989 1991 1993

Fiscal year

Ave

rage

pow

er (

W)

0.00

0.50

1.00

1.50

2.00

2.50

3.00

3.50

4.00

4.50

Ava

rage

EE

R (

W/W

)

Power EER

The falling rate of improvement from 1983 to 1993 was a major stimulus behind the introduction ofrevised targets in 1994. Another factor was the growing market share of reversible units, which arenow more common than cooling-only units.

1994 minimum energy efficiency targets

Air-conditioner efficiency policy is developed by MITI, which convenes an expert advisorycommittee charged with developing efficiency standards. The committee comprises mostly

6 Ibid

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academics who mediate between industry and government in defining the standard thresholds.7

There is no formal cost analysis as used in North America and Europe, and the whole process cantake less than a year. The new targets require only slight efficiency improvements to be met, butthey are expected to produce larger savings as manufacturers try to differentiate their products fromthose of their competitors.

The minimum energy efficiency targets that were set in 1994 are shown in Tables 5.3 and 5.4. Theyapply to the shipment-weighted average values of each producer or supplier and were required tohave been attained by October 1997. Almost all the models sold on the Japanese markets are split-packaged units8 and the targets are estimated to apply to 93% of all air-conditioner shipments. Thereference values shown in Table 5.4 refer to the sales-weighted average performance of Japanesecooling-only air-conditioners in 1992 while the values in brackets in both Tables 5.3 and 5.4 showthe minimum percentage EER or COP improvement required from the average 1992 values.

Table 5.3. The 1997 energy-efficiency target values for heat-pump (reversible) air-conditioners of≤27 kW capacity in Japan.9

Category and cooling capacity Cooling

EERc

Heating

COPh

Cooling plus heatingaverage [(EERc +

COPh)/2]

Integrated units

≤4 kW

Split systems

≤4 kW

4 kW < CC ≤7.1 kW

>7.1 kW

2.19 (3%)

2.67 (5%)

2.34 (3%)

2.45 (3%)

2.38 (3%)

3.20 (5%)

2.56 (3%)

2.62 (3%)

2.33 (5%)

2.97 (6%)

2.50 (5%)

2.59 (5%)

Abbreviations: CC = cooling capacity, EERc = EER in cooling mode, COPh = COP in heating mode.

Table 5.4 The 1997 Japanese target values for cooling-only air-conditioners of ≤27 kW capacity.

Category and cooling capacity Cooling EER 1992 reference EER

Integrated units

≤4 kW

4 kW < CC ≤7.1 kW

Split systems

≤4 kW

4 kW < CC ≤7.1 kW

>7.1 kW

Weighted average for all categories

2.45 (10%)

2.20 (8%)

3.09 (6%)

2.42 (11%)

2.45 (5%)

2.93 (6%)

2.23

2.04

2.92

2.19

2.34

Abbreviations: CC = cooling capacity; EER = energy-efficiency ratio.

The new ‘Top Runner’ energy efficiency thresholds announced in March 1999 and applicable from 7 Egan K, du Pont P. Efficiency standards and labeling in Asia: briefing paper [draft]. International Institute for EnergyEfficiency, Bangkok, March 1998. 8 Rosenquist R. ‘Technical aspects of window air conditioners.’ Presented at the Institute for International Education’sforum on Developing Effective Energy Efficiency Product Labeling Programs, Washington, DC, 26 March 1997. 9 Tanabe K. Standards and labeling activities in Japan. The Energy Conservation Center, Japan; presented at the Forumon Asia Regional Cooperation on Energy Efficiency Standards and Labeling, International Institute of EnergyConservation, Thailand, 14–16 July 1997.

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either 2004 or 2007 are shown in Tables 5.6 and 5.7.

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Table 5.6: Revised Japanese efficiency targets for heat pump air conditioners up to 27 kW, applicable from2004

Category Energy efficiency target

Cooling capacity ranges Cooling and heatingaverage

(EERc + COPh)/2 (W/W)

Split systems

CC ≤ 2.7 kW

2.7 kW < CC ≤ 3.3 kW

3.3 kW < CC ≤ 4.2 kW

4.2 kW < CC ≤ 7.25 kW

7.25 kW < CC ≤ 27 kW

5.27

4.88

3.63

3.15

3.10

Window systems 0 kW < CC ≤ 27 kW 2.85

Multi-split systems

CC ≤ 4.25 kW

4.25 kW < CC ≤ 7.25 kW

7.25 kW < CC ≤ 27 kW

4.12

3.23

3.08

Single-duct systems 0 kW < CC ≤ 27 kW 3.02

Other systems

CC ≤ 3.3 kW

3.3 kW < CC ≤ 3.9 kW

3.9 kW < CC ≤ 7.25 kW

7.25 kW < CC ≤ 27 kW

3.94

3.19

3.13

3.04

CC = cooling capacity

Table 5.7: Revised Japanese efficiency targets for cooling only air conditioners up to 27 kW, applicable from 2007

Category Energy efficiency target

Cooling capacity ranges EERc

(W/W)

Split systems

CC ≤ 3.3 kW

3.3 kW < CC ≤ 4.1 kW

4.1 kW < CC ≤ 7.1 kW

7.1 kW < CC ≤ 27 kW

3.64

3.08

2.90

2.81

Window systems 0 kW < CC ≤ 27 kW 2.66

Multi-split systems

CC ≤ 7.0 kW

7.0 kW < CC ≤ 27 kW

3.23

2.47

Single-duct systems CC ≤ 7.1 kW

7.1 kW < CC ≤ 27 kW

2.72

2.71

Other systems

CC ≤ 7.1 kW

7.1 kW < CC ≤ 27 kW

2.88

2.84

CC = cooling capacity

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5.4. The European market situation compared with other OECD countries

It is pertinent to this study to compare energy-efficiency levels of RACs sold in the EU with thosesold in other regions of the world.

Single-packaged RACs

Table 5.5 summarises the percentage and number of single-packaged (window/wall) models in theEurovent database that would satisfy the various MEES regulations around the world. In the case ofAustralia, which has not implemented MEES, the table indicates the Eurovent models that are abovethe average efficiency of the Australian market.

Table 5.5. EU window/wall air-conditioners that would satisfy other regions’ MEES and targets.

MEES or target thresholds Percentage ofunits passing

No. of unitspassing

No. of unitseligible

US 2000, louvered, cooling-only 0.0 0 16

US 2000, cooling-only, unlouvered 81.0 68 84

US 2000, reversible, louvered 25.0 1 4

US 2000, reversible, unlouvered 84.1 53 63

Philippines 2002 MEES, all 66.5 111 167

Taiwanese 1996 MEES, all 88.0 147 167

Japanese 1997 targets, cooling-only 85.0 85 100

Japanese 1997 targets, reversible 89.6 60 67

Korean 1997 targets, all 52.7 88 167

Korean 1991 MEES, all 74.3 124 167

Chinese 1989 MEES, all 87.4 146 167

Australian average, cooling-only, fixedA 78.0 78 100

Australian average, reversible, fixedA 86.6 58 67

A Australia has not implemented MEES: the values in the table indicate the percentage of EUmodels which exceed the average EER of Australian RACs.

Split systems

Table 5.6 summarises the percentage and number of split-packaged RACs in the Eurovent databasethat would satisfy the various MEES regulations around the world. In the case of Australia, whichhas not implemented MEES, the table indicates the Eurovent models that are above the averageefficiency of the Australian market. The NAFTA central air-conditioner MEES are not included asthey are calculated using a seasonal EER value that is not directly comparable with the European orISO 5151 test procedure.

Table 5.6. EU split-packaged air-conditioners under other MEES and targets

MEES or target thresholds Percentage ofunits passing

No. of unitspassing

No. of unitseligible

Japanese 2007 targets, cooling-only 2.3% 13 575

Japanese 2004 targets, reversible 9.7% 52 535

Japanese 1997 targets, cooling-only 35.3 203 575

Japanese 1997 targets, reversible 86.9 465 535

Korean 1997 targets, all 20.5 227 1110

Korean 1991 MEES, all 48.7 541 1110

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Chinese 1989 MEES, all 76.6 850 1110

Australian average, cooling-only, fixed A 43.8 252 575

Australian average, reversible, fixed A 87.9 470 535

A Australia has not implemented MEES: the values in the table indicate the percentage of EUmodels which exceed the average EER of Australian RACs.

Figure 5.5 shows the Eurovent EER data against cooling capacity data for the split systems, with theassociated international MEES thresholds.

Figure 5.5. Energy-efficiency ratios for split-packaged RACs in the Eurovent database and internationalMEES thresholds.

Conclusions from international comparison

The principal conclusion of this comparative work is that there has been considerable legislativeactivity to improve air-conditioner efficiency and that a large proportion of RACs currentlyavailable for sale in the EU would not satisfy efficiency requirements in many other countriesaround the world. This suggests that there is significant scope to improve RAC energy performancein the EU and that to do so requires not technological innovation but merely implementation ofwell-established higher-efficiency design options. European or national efforts reported previouslyin this report appear very limited when compared with the schemes being applied in any country orgroup of countries considered here.

1.2

1.6

2.0

2.4

2.8

3.2

3.6

4.0

4.4

4.8

5.2

1 2 3 4 5 6 7 8 9 10 11 12Cooling capacity (kW)

EE

R (

W/W

)

Split, cooling only, air

Split, cooling only, water

Split, reversible, air

Japanese 1997 targets, coolingonly

Japanese 1997 targets,reversible

Korean targets, all

Korean MEES, all

China MEES, all

Australia average, cooling,fixed

Australia average, reversible,fixed

Japanese 2007 targets, coolingonly

Japanese 2004 targets,reversible

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6. PROJECTIONS TO YEARS 2010 AND 2020 (BAU SCENARIO) 6.1 Computation of energy consumption of appliances

The main problem for computing consumption is that there is very little information available onthe actual use in the field of room air-conditioners in the residential sector within the EuropeanUnion. No public results of measurement campaigns (which are very helpful, even if they refer onlyto a few number of households) are available.

Computer models to simulate the performance of RACs

A de-coupled approach (building/system) has been used in this study. In the first instance, coolingneeds (sensible + latent) have been computed using COMFIE, a dynamic multi-zone buildingthermal simulation program, after which the electricity consumption has been derived from thesimulated cooling needs and from the known performance characteristics of one of the RACsinvestigated. This means that it is assumed that the specific cooling needs are independent of thecooling system

Methods that take into account variations in RAC energy performance related to outsidetemperature and humidity on the basis of T1 conditions only were required, since T2 testingconditions are not widely used. It was decided to develop some simplified methods based on morecomplex computer models. The two modular heat-pump computer models that were extensivelyexamined, evaluated and used are the American ORNL Heat Pump Design Model – Mark V(Version 95d) and the French Modelisation Modulaire Windows (MoMo Win) (Version 1.5). Thetwo software tools were developed using the same modular philosophy, e.g. the various parts of aheat pump (compressor, evaporator, condenser, flow control devices and connecting lines) arecharacterised independently and then linked in order to describe the overall performance of the heatpump. However, the information that needs to be input into each software tool to characterise a heatpump is almost the same. The major difference between the two models is the manner in which thecompressor performance is modelled.

From the individual RACs to the stock of RACs

Due to the variations in RAC use, it was important to simulate the dynamics of RAC operation infunction of time (day, months) and to check the final impact on electricity companies’ peak demand.Another piece of software by Armines has been used for simulating load aggregation and finalconsumption.

The software MURELEC by Inestene has been used to analyse the expansion and renewal of RACstocks. The purpose of MURELEC (Modèle d’Utilisation Rationnelle de l’Energie Electrique –model of rational use of electricity energy) is to evaluate trends in specific electricity consumptionand to measure the impacts of eventual actions of demand-side management on energy efficiency.

Data for all these steps are numerous. They have been obtained through ‘national questionnaires’,from existing climatic databases and from Eurostat.

Part-load performance

The results of testing according to EN 814 was the basis of our study. For our study it was equallyimportant to establish a link between such nominal performance and part-load (or non nominaltemperature) performance. We have computed a number of functions F, each of them representativeof a cluster of appliances, which link the electrical power demand to the cooling capacity and to thevalues of the indoor and outdoor temperatures (T) and humidities (w). P F(P ,T ,w ,T ,w )E C OUTDOOR OUTDOOR INDOOR INDOOR=

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The energy efficiency ratio under these given conditions can be calculated for each hour of each dayof the week.

Moreover two coefficients of degradation because of fouling and on-off cycles of the airconditioners were introduced10.

The degradation coefficient for cycling is defined as below.

Cd=F

EERss

EERcyc

1

)1(

with Cd=0.25 and EER cyc(cycle) < EERss(steady state).

Condenser and evaporator fouling is a substantial cause of performance degradation of airconditioners. The impact on the EER is to be determined on the whole life cycle of the machines(10-13 years). According to an article in HVAC&R research11, a blockage of 56% of the face area ofthe condenser of a rooftop air conditioner results in a reduction of 18% of EER. In the same way,EDF12 noticed that the performance of a tested split could decrease by more than 30% with areduction of the nominal air flow of the condenser by 50%. That is the reason why it is estimatedthat, as an average value, the EER is reduced down to 20 % because of air conditioners faults

For each base-case simulation, the total energy consumption is given when summing the powerdemands (see fig 6.1). Two coefficients ((5/7)*365/12 and (2/7)*365/12) are applied in order toweight the week and weekend days. P PE,TOTAL E

HOURS

= ∑

Fig 6.1 Behaviour of the four studied models

The equivalent number of hours at the nominal rating conditions is then calculated by the followingformula:

10 O’Neal D.L., Katipamula S., Performance degradation during on-off cycling of single-speed air conditioners and heatpumps: model development and analysis’, 1991,. ASHRAE Transactions part B, p. 316-323 11 M. Breuker&J. E.Braun, Common faults and their impacts for rooftop air conditioners, July 1998, HVAC&RResearch, p.303-318 12 J.M. Taldir, Le fonctionnement des climatiseurs individuels split et windows dans les conditions des DOM, Août1996, DER-EDF

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nP

PEQUIVALENTE,TOTAL

E,RATING

=

RATING is referring to T1 conditions

Presentation of results

As the number of technical options studied and the number of models are numerous, it is notrealistic to perform the technical-economical analysis on each of the base-case simulations.Consequently, unitary results have to be aggregated in terms of zones and sectors. An EU-averagehas then been considered, knowing that the optimum is in fact varying from one country to another,and from one sector to another. The average equivalent number of hours is given by:

n nEQUIVALENT,AVERAGE EQUIVALENT= ∑SECTORS ZONES,

In the previous equation, it was decided to weight by the market share of the considered sector andzone.

The number of running hours under nominal conditions (Table 6.2 )will allow us to calculate thepayback of different technical solutions thanks to a life cycle analysis.

Table 6.2: number of hours of operation resulting from computation

Commercial Office Household Hotel

Austria Salzburg 177 193 74 235 153Austria Vienna 134 147 55 176 116France Carpentras 1414 1307 547 595 1028France Limoges 790 726 212 314 544France Trappes 752 625 156 262 468Germany Middle 431 383 168 236 264Germany North 199 187 87 115 129Greece Athens 984 891 741 1530 888Greece Theso 859 729 480 1175 742Italy Cagliari 1265 993 822 898 1057Italy Milano 1017 727 615 726 819Italy Napoli 1366 966 833 1097 1104Portugal Lisbon 1226 931 611 413 851Spain Murcia 2157 1402 1049 1870 1494Spain Oviedo 678 300 143 382 338UK London 230 276 94 331 247

Weighted averageNumber of hours at constant EER

We have then defined an average (weighted by the penetration rates in each climatic zone) numberof hours per sector.

Table 6.3 Weighted number of hours for the calculation of energy consumption

Commercial Office Household Hotel1019 803 519 768

Weighted number of hours

773All sectors

Detailed values for RAC use in households are specially important for our study. They take the formof an equivalent number of hours of figure 6.2.

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Figure 6.2 variations in operating time

Number of hours of air conditioning in the residential sector

156

87

168

615

833

741

4808221049

143

611

212

547

94

74 55

The case of water-cooled appliances

When they are used with water coolant the appliances have about the same operating time. If thewater is lost water (either drinkable or not) the EER remains even more constant than with aircooled appliances, so it remains far better than with air cooling and applying the same number ofhours may seem first too tough and that these appliances behave better than computed.

However, a number of the water cooled appliances are not used autonomously. We may assume thatin the case of closed loops, a 20K penalty is typically originated by the heat exchangers. A roughestimate of EER loss (based on EER sensitivity described previously for air cooled units) gives to a2 %/K performance loss in that case, so a 0,4 performance drop. This performance penalty is takeninto account by applying the same operation duration to water cooled appliances which has beencomputed for air cooled appliances..

On total, having in mind that a few percent only of european appliances are in that category and thatthere are situations both ways, it is not a big source of uncertainty to apply to all appliances theoperating duration computed for air cooled appliance.

6.2 Stock and market in 1990, 1996, 2010 and 2020

A basecase scenario (Business As Usual) has been defined in order to analyse the technical andeconomical potential of single or combined measures in several alternative energy efficiencyscenarios. The year 2010 has been chosen for projection due to the Kyoto deadline. A longer termindication is given for year 2020. For the past, study has been mostly done for 1996 but also for1990 for consistency with Kyoto conventions.

Evolution of the market

As already described, the extrapolations werebased on 1996 figures and national evolution trends.Seven types of appliances were treated separately, for which the starting point is geiven in Table6.4.

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Table 6.4: RAC types and 1996 market13

RAC categories % of models % of sales

MS,A: Multi-split, Air cooled 7.8 7.0

SP,A: Split, Air cooled 77.3 68.7

SP,W: Split, Water cooled 0.3 0.3

PA,A: Packaged, Air cooled 4.0 2.2

PA,W: Packaged, Water cooled 7.1 3.8

SD,A: Single-duct, Air cooled 2.0 13.8

SD,W: Single-duct, Water cooled 0.6 4.2

TOTAL 100 100

Our assumptions, based on CECED recomendations, correspond to approximately half of thepotential ownership foreseen by Eurovent for 2020, a conservative hypothesis. We have also takeninto account the market trends of the four equipment as observed on the italian market, the mostmature one, shown on Table 6.6. CECED has indicated that this evolution, and namely the decreasein Single Ducts market shares, would become general in all countries.

Table 6.6: Evolution of Italian RAC sales to 2020 according to ANIE/COAER

Type of RAC 1996market

2020 market 2020 stock

Single Duct 9.59%

2.64% 3.30%

Split 82.68%

91.14% 90.09%

Multi Splits 3.11%

1.66% 4.61%

Packag. Units 4.63%

4.56% 2.00%

Total 100%

100% 100%

The following table indicates this extrapolation.

Table 6.7 Projected share of RAC sales (% of total market)

Market

1990

Market

1996

Market

2000

Market

2010

Market

2020

13 "Models" ratio between water and air cooled units was kept for "market" figures

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Multisplits 4% 7% 14% 14% 14%

Splits 60% 69% 66% 71% 77%

Packaged 19% 6% 7% 6% 4%

Single Ducts 17% 18% 13% 9% 5%

TOTAL 100% 100% 100% 100% 100%

Finally used with a stock model, this leads to the results of Table 6.8.

Table 6.8 Share of RAC types in 2020 stock (% of whole stock)

Single Duct Window Split Multi-Split

Italy 3.30% 2.00% 90.09% 4.61%

Spain 4.49% 6.23% 70.97% 18.31%

Portugal 0.65% 2.55% 81.37% 15.43%

Germany 23.13% 9.58% 52.80% 14.49%

Greece 0.00% 0.39% 91.77% 7.83%

France 8.35% 4.48% 68.86% 18.31%

UK 7.32% 1.99% 71.16% 19.53%

Austria 4.92% 14.56% 51.86% 28.65%

Other EU ** 3.74% 15.04% 51.30% 29.92%

Results on stocks in use and market

The number of units in use in the various countries increases greatly over simulated years. Tables6.9 to 6.11 give the splitting according to categories, sectors and countries.

Table 6.9 Stock by type and yearly growth

Stock

1990

Stock

1996

%/year

90/96

Stock

2010

Stock 2020 %1996/

2020

Multisplits 115516 981313 42.8% 3 567 177 5 597 448 7.5%

Splits 687184 4517047 36.9% 14 627 802 22 953 264 7.0%

Packaged 205227 688477 22.4% 1 270 715 1 993 946 4.5%

SingleDucts

164435 1215945 39.6% 1 556 982 2 443 143 3.0%

TOTAL 1172362 7402662 36.0% 21 022 676 32 987 801 6.4%

Very conservative assumptions have been made about future market growth.

Table 6.10: Estimated stock of appliances by country and yearly growth

1990 1996 2020 1990/

1996

1996/

2020

Austria 8600 79000 849144 44.7% 10.4%

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France 368700 1259100 6353694 22.7% 7.0%

Germany 144100 526100 4664828 24.1% 9.5%

Greece 76000 744830 3039588 46.3% 6.0%

Italy 198900 2111740 3084364 48.3% 1.6%

Portugal 136670 322820 1300000 15.4% 6.0%

Spain ? 1369000 7800051 ? 7.5%

UK 153112 674412 3097236 28.0% 6.6%

Others 86280 315660 2798897 24.1% 9.5%

EU 1172362 7402662 33777613 36.0% 6.5%

The total number of units in the European Union is multiplied by 18 in the period covered by theKyoto protocol. Some countries like Spain follow a quicker evolution. Associated electricityconsumption will grow in a similar manner.

6.3 Electricity consumption

The base case computed here is the BAU scenario previously defined.

Description of performance data used

In order for the model to calculate the accurate consumption related to the exact stock of appliancesof each of the four equipment, the shares of Split, Multi-Split, Single-pckaged and Single Duct havebeen input into MURELEC. They are combined with the energy consumption values derived fromthe Chapter 4 (average size per type).

Table 6.12: Electrical consumption for 1996 per type

Category Description Pc Pe EER

MS1 Multi-split, 230 V, cooling-only, air-cooled 5.23 1.98 2.70

MS2 Multi-split, 230 V, reverse, air-cooled 5.42 2.15 2.53

MS3 Multi-split, 400 V, cooling-only, air-cooled 7.00 2.71 2.66

MS4 Multi-split, 400 V, reverse, air-cooled 6.48 2.77 2.34

MS All air-cooled multi-splits 5.56 2.16 2.63

S1 Split, 230 V, cooling-only, air-cooled 4.87 1.98 2.53

S2 Split, 230 V, reverse, air-cooled 4.93 2.04 2.48

S3 Split, 230 V, cooling-only, water-cooled 7.66 3.19 2.40

S4 Split, 400 V, cooling-only, air-cooled 8.24 3.35 2.46

S5 Split, 400 V, reverse, air-cooled 4.53 1.64 2.75

AirS All air-cooled splits 5.28 2.16 2.48

WaterS All water-cooled splits 4.53 1.64 2.75

P1 Single-packaged, 230 V, cooling-only, air-cooled 4.92 1.55 3.32

P2 Single-packaged, 230 V, reverse, air-cooled 3.66 1.18 3.20

P3 Single-packaged, 230 V, cooling-only, water-cooled 4.36 1.90 2.38

P4 Single-packaged, 230 V, reverse, water-cooled 10.41 4.36 2.44

P5 Single-packaged, 400 V, cooling-only, air-cooled 10.27 2.90 3.55

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P6 Single-packaged, 400 V, reverse, air-cooled 5.79 2.54 2.32

P7 Single-packaged, 400 V, cooling-only, water-cooled 10.38 4.43 2.38

P8 Single-packaged, 400 V, reverse, water-cooled 11.23 3.15 3.67

AirP All air-cooled packaged units 7.20 3.08 2.38

WaterP All water-cooled packaged units 5.40 1.65 3.32

AirSD Single-duct, 230 V, cooling-only, air-cooled 1.70 0.81 2.07

WaterSD Single-duct, 230 V, cooling-only, water-cooled 2.09 0.88 2.33

Results on consumption

Electricity consumption due to RAC is given in figure 6.3 and Tables 6.13 and 6.14 according tosectors and countries.

Table 6.13: Electricity consumption by economic sector (GWh/year)

Sector 1990 1996 2010 2020

Households 387.2 2445.5 7483.3 11375.6

Offices 538.0 3398.1 8544.7 13321.2

Small business 735.8 4647.1 9553.7 14339.5

Hotels 266.9 1685.4 3577.4 5393.8

Total 1927.9 12176.2 29159.1 44430.2

Figure 6.3 Growth of energy consumption

E vo lu tio n o f R A C c o n su p tio n p e r s ec to r - B A U s cen a r io

0

5 00 0

1 00 0 0

1 50 0 0

2 00 0 0

2 50 0 0

3 00 0 0

3 50 0 0

4 00 0 0

4 50 0 0

1 99 6 2 00 0 2 00 5 2 01 0 2 01 5 2 02 0

in G

Wh

h o te ls

sm a ll b us in ess

o ffice s

h ou seh o lds

Table 6.14: Energy consumption of RACs by country (GWh/year)

1990 1996 2010 2020

Austria 68.6 121.3 235.0 364.5

France 331.6 1782.1 5517.2 8975.5

Germany 155.9 672.4 1914.0 3197.3

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Greece 208.8 1006.6 2281.3 3478.6

Ialy 761.0 4494.1 5743.6 7033.9

Portugal 162.4 713.8 1806.8 2552.2

Spain not av 2496.4 9366.4 15146.6

UK 120.0 446.0 1135.7 1783.8

Other EU 119.6 443.5 1159.1 1897.7

Total EU 1927.9 12176.2 29159.1 44430.2

Contribution to Electricity peak Demand

Electricity demand due to RAC is computed on the basis of the dynamics of the RAC units. Part ofthe peak demand is coincident with the grid peak.

Figure 6. 4 Load curve trend

L o a d f o r a n a v e r a g e w e e k d a y o f a u g u s t - B A U s c e n a r io

0

5

1 0

1 5

2 0

2 5

3 0

3 5

4 0

4 5

1 3 5 7 9 11 13 15 17 19 21 23

in G

W 1 9 9 62 0 2 0

Table 6.15: Load peak per economic sector

Unit: GW 1996 2010 2020

Households 4.91 15.29 23.76

Offices 1.35 2.45 3.51

small business 2.03 4.19 6.38

Hotels 2.06 5.53 9.55

Total 10.34 27.46 43.21

Table 6.16: Load peak per country

Unit: GW 1996 2010 2020

Austria 0.01 0.20 0.40

France 0.86 2.81 4.58

Germany 0.24 1.43 2.51

Greece 1.72 4.23 6.74

Ialy 4.25 5.52 6.94

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Portugal 0.46 1.26 1.84

Spain 2.62 11.01 18.04

UK 0.04 0.14 0.65

Other E.U 0.14 0.85 1.50

Total E.U 10.34 27.46 43.21

6.4 – Environmental impact

Environmental impacts of RAC take place in the atmosphere: acid pollution, ozone depletion, greenhouse gases emission, but some specific effects can also be mentioned (solid waste, water use).

Global Warming

There are direct effects of RAC on global warming (refrigerants release in atmosphere) and indirecteffects (energy consumption over their life time). R22 is the most commonly used RAC refrigerant;however, as this fluid has an ozone-depletion and a global warming potential its production will beprohibited in developed countries. Some RACs already use alternative refrigerants such as R290,R407C, R-134a and R-410a (these refrigerants are more or less compatible with the runningparameters of a traditional R22 unit). In fact, a higher energy efficiency and a more environmentallybenign refrigerant will both result in a lower contribution to global warming. TEWI (total equivalentwarming impact) is the integrated index used to measure the global-warming impact of all gaseousemissions, including those from direct and indirect sources. TEWI can be easily computed fromknown figures.

However, our study group was not in charge of the issue of change of refrigerants. The directcontribution of RAC to global warming will drop independantly from our action. The only unsolvedproblem is to know if technical potential will remain the same after the refrigerants change, and ifthe manufacturers can accomodate the sped of change generated by the various policies of the EU.We shall concentrate here on our possible range of actions: energy consumption changes resulting ina lower indirect CO2 release. Since there is a European bubble, one could only consider the averageCO2 content of the European kWh, set to 440 gCO2/kWh, the OECD average. In fact, the exactfigure for CO2 content per kWh were avilabel for each country, this was taken into account.

Water use

In a similar way, the use of drinkable (or not drinkable) water by water-cooled RACs can be easilycomputed from known data. All these data should be used in an environmental impact assessment.

Since few people have access to industrial water or to a private well, water-cooled RAC use mostlydrinkable water or need a close loop on a cooling tower. This data not being available, it wasestimated that 20% use drinkable water, 60% use a closed loop and 20% some other solution, liketheir private well. The use of waste water for heat rejection is foreseen in research projects (Milano).

In the case of closed loop a 20K penalty is originated by the heat exchangers. This has been alreadymentionned and estimated. It is taken into account by applying to the water cooled units the sameoperating duration as to the other types.

Something should be said about the case of drinkable water use. The figures in kWh and EER takenfrom 6 representative models allow the estimation of the water used per year, and per cooling kW as37 m3. On the basis of a conservative estimate of the market penetration (20 %) the total drinkable

water use for the purpose was at least 40 000 000 m3 for year 1996 in Europe, a figure that will bemultiplied by 4 by year 2020. Such figures correspond to the use of water of a medium size city

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(100000 to 500000 inhabitants) and treatment costs over 100 Meuro. For these appliances, the billfor water will be of the same size as for electricity. A way for warning the buyer should be found.

Regional atmospheric pollution

Atmospheric pollution from power plants is composed of dust, NOx and SO2 which have a regionalimpact and CO2 with a world wide impact. We have admitted here that European regulation on acidpollution was well designed and applied and that a specific effort on acid pollution was not part ofour objectives. It is different for CO2; the Kyoto protocol is recent and its full implementation inEurope not yet achieved; furthermore there is a European bubble and the trends or measuresconsidered here can gave directly positive or negative consequences on the achievement of theEuropean objectives.

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Results on CO2 emissions

The emission of CO2 in Europe due to RAC have been summarised in Table 6.17.

Table 6.17: Emissions by country

Unit: tonnes CO2 1990 1996 2010 2020

Austria 5 186 9 170 17 765 27 554

France 17 226 92 578 286 612 466 267

Germany 25 358 109 369 311 321 520 055

Greece 151 686 731 261 1 657 288 2 527 087

Ialy 389 162 2 298 202 2 937 174 3 597 010

Portugal 94 768 416 537 1 054 355 1 489 331

Spain not av (may be300 000)

1 171 211 4 394 340 7 106 179

UK 76 197 283 201 721 146 1 132 676

Other E.U 19 453 72 137 188 533 308 669

Total E.U 779 037 5 183 665 11 568 532 17 174 827

The emission of CO2 in Europe due to RAC is multiplied by 11 in the time of the Kyoto protocol.The additional emission due to this type of appliance is about 10 out of the 3000 tonnes of the initialemissions by fuels in the EU. The direct effect of the growth of this market on total EU emissions is+0,33% to be compared with the -8% target.

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7. TECHNICAL–ECONOMICAL STUDY OF OPTIONS 7.1 Technical definitions: the four real appliances used, their physical modelling and its validation

Measures for improving RAC energy efficiency are of three main types:

improvement of component performance (better compressor, fan etc.)

optimised design (optimised system temperatures, pressures etc.)

improved operational control.

Our study is based on the EN 814 standard previously described, which doesn’t yet cover allconditions. Until its extension as a result of mandate M/274, it is necessary to use a computermodel, in our case ORNL Mark V, to extend testing results. The use of improved components andoptimised design will show results at any load and therefore their benefits will be reflected bothunder the EN 814 test and in our ORNL computations. For instance, a better compressor will give abetter EER. Split units can use three types of compressor: (i) conventional reciprocatingcompressors (one piston in a chamber), (ii) rotary compressors (with a ‘rolling’ compressible spacein a circular chamber) and (iii) in the upper power range, scroll compressors (two spirals creatingcontinuous compression at high efficiency).

Scroll compressors are capable of operating at different speeds and are becoming more commonamong RAC models. However, not all the benefits they bring are measurable when the present EN814 test protocol is used, which leads to a control problem: how should inverter-driven variable-speed compressors with significantly higher part-load performance be dealt with? Inverters rununder an adjustable frequency (from 40% to 120% of the nominal value), resulting in varyingcompressor speeds (and, as a result, fan speed).

Representation of appliances by four specific units

As already described, the appliances studied were divided into seven types:

Table 7.1: RAC selected for technical analysis

RAC types RAC model studied Share of sales (%)

01 MS,A: Multi-split, air-cooled - 7.0

02 PA,A: Packaged, air-cooled - 2.2

03 PA,W: Packaged, water-cooled - 3.8

04 SD,A: Single-duct, air-cooled C 13.8

05 SD,W: Single-duct, water-cooled - 4.2

06 SP,A: Split, air-cooled A, B, D 68.7

07 SP,W: Split, water-cooled - 0.3

TOTAL 82.5% 100.0

From the seven categories, four specific models close to the centre of some representative ‘clusters’were selected for technical analysis: three very different models from the largest category (splits,69% of the market) and one from the second largest category (single ducts, 6% of stock, 14% of themarket). No multi-split model was chosen because they are similar to splits, nor were any modelsfrom the less numerous packaged unit categories.

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Table 7.2. The four models investigated.

Unit Type (according to 4-part clustering process)

A S5: Split, 380 V, reverse, air-cooled

B S1: Split, 220 V, cooling-only, air-cooled

C SD1: Single-duct, 220 V, cooling-only, air-cooled

D S4: Split, 380 V, cooling-only, air-cooled

All the models studied in detail were air-cooled. In fact, water-cooled appliances are not reallyautonomous – they rely on communal or private water (with associated costs and environmentalimpacts) or they use a secondary heat exchanger in the outside air (with consequent investment,temperature and EER penalties). This is described above.

Performance data used

Two types of questionnaire, one for air-cooled and one for water-cooled systems, were compiled inorder to collect the technical data and establish the parameters required for the modelling of theexamined air-conditioners. The questionnaires were submitted to the European associations of roomair-conditioner manufacturers, which then undertook the task of contacting the manufacturers of theselected representative units (or of other similar units in case it was not possible to obtain the datafor the specific model) and providing us with the required data. The manufacturers provided theworking party with complete data for four units and thus only these units were studied.14

At first the EER of each model (in its present state) was calculated and compared with the onemeasured under standard test conditions as submitted to us by the manufacturers. The results areillustrated in Table 7.3:

Table 7.3 Comparison of calculated and manufacturers’ submitted EER

Unit Measured EER Calculated EER

A 2.66 2.72

B 2.43 2.48

C 1.90 1.92

D 2.60 2.75

It can be seen that for three of the simulated units (A, B and C) the calculated EER is in very goodagreement with the measured values (2%, 2% and 1% difference, respectively), while the differencebetween the calculated and measured EER value of unit D is higher (6%). This difference is due tothe fact that not all the required information was available for this unit and thus default typicalvalues were used in this case. In conclusion, the modelling of the units is successful and thus theORNL software can be used confidently to simulate the performance of the examined units after theapplication of the proposed improvements and to evaluate their efficiency.

7.2 Options and technical results

Next, the impact of each of the proposed improvements to the units’ overall performance wassimulated by calculating each unit’s EER after the application of the intervention and under standard

14 It must be noted that data for three other units were submitted, but as these data sets were not complete and a lot ofcritical information was missing it was not possible to simulate the performance of these units as well.

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test conditions. In order to do this, the required modifications were input into the software for eachscenario. However, it was not possible to simulate directly all the scenarios, because of thesoftware’s limitations, and details from existing literature were also used in some cases.

General results

Various technical options and their effect on EER are shown in Table 7.4.

Table 7.4. Average gain per option (averaged over the four models)

Option Technical improvement Average increase in EER (%)

1(a) Increase frontal coil area (15%) 4%

1(b) Increase frontal coil area (30%) 8%

1(c) Increase frontal coil area (45%) 11%

2(a) Add one refrigerant tube 10%

2(b) Add two refrigerant tubes 16%

3(a) Increase fin density (10%) 10%

3(b) Increase fin density (20%) 16%

4 Add subcooler to condenser coil 1%

5 Improve fin design (modify fin pattern) 11%

6 Improve tube design 8%

7(a) Use of a high efficiency fan motor 1%

7(b) Use of an electronically commutated motor 2%

8(a) Improve compressor efficiency (5%) 3%

8(b) Improve compressor efficiency (10%) 5%

8(c) Improve compressor efficiency (15%) 8%

9 Use of R410a with optimised system 5%?

10 Use of variable speed compressors 12%

11 Use of electronic expansion valves 5%?

12 Use of (fuzzy) controls 4%?

Specific problems of variable speed technology (inverters)

The use of variable speed (inverter-type) compressors instead of single frequency ones could lead,according to some, to seasonal cooling energy savings ranging from 10% to 40%. A review of theliterature on the energy savings due to the use of inverter technology in room air-conditioners hasbeen made but suggests that there is not enough evidence to completely support such high figures.

Table 7.5. Studies of inverter use and reported energy savings

Reference Study type Studied mode Power (kW) Energy saving (%)

[SENS85] Experimentation Heating 4.4 29

[MILL88] Experimentation Cooling/heating 8.8 15–20

[MACA88] Simulation Heating 15

[HORI85] Experimentation Cooling/heating 3.0 15

[TORI87] Experimentation Heating 6.9 7-15*

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[SENS89] Simulation Cooling 14.5 30

[SHIM85] Simulation Heating 6.3 20–40

[PARK88] Experimentation Cooling 3-5 17–18*

[LBNL96] – Cooling 10**

* Gains in terms of EER (or COP) and not in energy consumption.

** The report states that ‘a conservative value’ has been taken into account.

The difference in physical behaviour of ‘inverter’-type RACs lies in their variable speed operation,for which EN 814 testing is not enough, and so experts could discuss further the reproducibility ofresults. Our estimation of the energy efficiency of inverter-type RACs is based on the report of onesingle manufacturer on the differences between nominal behaviour (as in EN 814) and practicalbehaviour. Despite the magnitude of the possible gains, this lack of reproducibility should preventthe Commission from immediately promulgating the benefits to be gained by using this type ofappliance. In the medium term, the outcome of the mandate M/274 to CEN and CENELEC willprovide an experimental basis enabling the evaluation of variable speed equipment.

As mentioned above, manufacturers claim that inverters result in energy savings of between 20%and 40% compared with a traditional unit. Inverters are reported to allow a quicker (as a result ofthe available 120% frequency) and stricter (because the unit generally runs 100% of the time)control of the indoor set temperature. This may produce a significant gain in comfort but notnecessarily a gain in energy savings. Reliability could also be affected.

A description of the main sources of energy gain achieved with an inverter follows here. Bylowering the compressor frequency, the flow rate of the refrigerant fluid decreases, therebydecreasing the high pressure level. With the resulting lower compression ratio, the electrical powerinput to the compressor is reduced. As the total cooling capacity is lower, the unit will run longerthan a conventional RAC in cycle mode, but with a greater EER. A secondary source of energy gainin inverters is that since they generally run 100% of the time, they avoid energy losses resultingfrom restarting that are found with conventional compressors.Most of these benefits could also beobtained by using certain kinds of multi-speed drives, which have not been tested on RACs but haveon other appliances like refrigerators.

On the other hand, there is concern about the continuous operation of the fan and possible electricconversion losses, which should not be disregarded in the extension of EN814 testing.

The increase in energy performance (EER) of an inverter-driven air-conditioner at part load isshown in Figure 7.1.

Figure 7.1. Benefits reported by one manufacturer for inverter RACs15.

15 The figure is taken from the TNO (1998) interim report.

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2

3

4

5

6

7

0.5 0.6 0.7 0.8 0.9 1.0 1.1 1.2 1.3

CAPACITY ratio

C.O.P.(cooling)

Ambient temperature 10 dgr.C

Ambient temperature 18 dgr.C

Ambient temperature 31 dgr.C

To gain an idea of the order of magnitude of potential gains and in order not to delay progress, datafrom one manufacturer was analysed and gave 10–12% as a preliminary estimate of weighted gainsby comparing the non-nominal behaviour of the ORNL simulated units and the non-nominalmanufacturer-reported values.

Potential gains have been evaluated in six simulations. For each of them, two figures are given,according to the value chosen for the coefficient of degradation due to on-off cycles applied to non-inverter units. The lower estimate (minimum) is obtained with Cd=0 (no performance degradationdue to cycles; all the gains are from constant adjustment of LP and HP levels). The upper estimate(maximum) is obtained with Cd=0.25.

Table 7.6: Gains with inverters over a full cooling season, computed here

Potential gain in terms ofaverage EER (%)

Country Sector Min Max

France Small businesses 15 36

Offices 12 29

Households –3 16

Italy Small businesses 15 36

Offices 15 41

Households 9 28

We continued the study assuming an estimated 10–12% gain. Further research, as well as the resultsof mandate M/274, will soon bring new evidence. Any remaining uncertainty arises from theimperfect definition of the quality of control.

Energy consumption of single-duct appliances

The question of whether energy consumption of single-duct RACs can be estimated with the samecomputational rules as splits, multi-splits and window units has been raised by the manufacturers’associations.

By using a hole in the window, the gap in a window that is partly open or a hole in the wall, single-ducts are likely to be easier to install by consumers themselves. In some cases single-ducts are notcomparable in use to split units for visual reasons (e.g. in historic centres) or for mobility reasons(mobility of residents, mobility within one house). Other technical solutions exist in each case toeffect cooling (multi-split or central air-conditioners in historic centres; mobile splits) but single-ducts are less expensive to purchase and easier to install and to move (outside manpower would be

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needed to obtain the same result with the other systems). So the real question is to compute theirenergy consumption.

Their efficiency is generally lower in test conditions. Many experts think that even larger over-consumption occurs in field situations because of air infiltration. As no published evidence wasavailable, a computer simulation was made.

The difference in physical behaviour of single-ducts lies in their integration with the roomventilation. Both units are inside the room and the condenser heats air which is extracted from theroom and rejected, creating an additional ventilation. The air extracted by the RAC is replaced bythe same quantity of outside air both in test and in real situations.

Single-ducts create low pressure in the cooled room, causing infiltration:

from outside (α)*(air flow rate treated)

or from another room of the building. (1- α)*(air flow rate treated)

This infiltration is high. For a 2 350 W unit, the air flow rate treated is typically 350m3/h, as opposed to 50–100 m3/h for natural ventilation. So, part of the time (when the ventilator operates) cooling loads areincreased:

Total cooling loads = Cooling loads needed to maintain set temperature in the room + Cooling loads dueto additional air leakage from outside + Cooling loads due to additional air leakage from another room

We have computed the field energy consumption of single-ducts on the basis of the simple physicalmodel of ventilation just described. We have found that, depending on climatic conditions, thebehaviour of single-ducts is in the range of –12% to +7% from the value computed by applying tothem the computational rules defined for the other RACs. Performance is better in northernclimates, where the single-duct provides additional ventilation, and worse in southern countries likeItaly (the bottom of the range here). Computations have not been done for Spain and Greece, forwhich over-consumption could reach 15%.

Some physical uncertainties also remain concerning the reproducibility of test results, though themandate M/274 to CEN and CENELEC and some collective effort on the part of manufacturers willsolve these in the medium term. This shouldn’t prevent us from using manufacturers’ reported datafor a while yet.

Summary of technical combinations

Evidently the potential savings decrease as more technological options are added since less energy isavailable to be saved (or less EER is available to be improved) due to the impact of the previouslyadded option(s). The most important combinations of technical options were completely re-simulated, so that no assumption could be made when considering combined EER increases.Therange of possible combinations is the as follows:

Table 7.7 Gains for sets of improvements

TECHNICALFEATURE

Optionsconsidered

EFFECT ONEER OF A

EFFECT ONEER OF B

EFFECT ONEER OF C

EFFECT ON EEROF D

AVERAGEINCREASE (%)

EXISTING APP. - 2.72 2.48 1.92 2.75

HEATEXCHANGERS

1b, 2b, 3b,5,6

3.80 3.69 2.93 3.88 46

COMPRESSOR 8c 2.94 2.68 2.04 2.97 8

HE+

COMP

1b, 2b, 3b,5,6, 8c

3.94 3.79 2.99 4.01 50

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ALLSCREENEDOPT.

1c, 2b, 3b,5,6, 7, 8c

3.97 3.81 3.00 4.04 51

INVERTERTECH ALONE

10 3.05 2.78 2.15 3.08 12%

HE + COMP +INVERTER

1b, 2b, 3b,5,6, 8c, 10

4.12 3.93 3.09 4.19 56%

ALL +INVERTER

1c, 2b, 3b,5,6, 7, 8c, 10

4.14 3.95 3.10 4.21 57%

Best on marketin class

- 3.20

(+20%)

3.56

(+46%)

3.09

(+63%)

3.25

(+25%)

+37%

In the case of inverters the improvement reflected here by a better nominal EER is in fact animprovement on seasonal EER which has been applied here in a rough manner, in order tosummarise information.

7.3 Economic calculations for the screening of cost-effective measures

The economic analysis was performed estimating the net benefits of the technological options of thevarious models to consumers. This needs a careful study of costs and overcosts and the use ofcriteria like net present value of investment or minimum life-cycle cost.

Study of costs and overcosts

RAC models base-case values are given in Table 7.8 for three of the four appliances studied. Thecosts are without margins.

Table 7.8 Starting point for the three models optimisation

Total cost Pc Pe EER Energy Cons. SpecificEnergy Cons.

(EURO) (kW) (kW) (kWh/y) (kWh/y/m2)

Model B 485 5.25 2.16 2.43 1 102 21

Model C 361 1.22 0.64 1.9 327 27

Model B-2 520 5.12 2.14 2.39 1 093 21

The individual costs of changes given by the manufacturers’ survey are summarised below in theform of a range. For the upper limit conservative options have been taken, such as the fact of takinginto account the overcosts in the thermodynamic parts and not the undercosts in the electrical parts(motors, compressors etc.) that are generated by a smaller electric consumption for the samenominal cooling capacity and the higher possible margins in improvement.

In fact the normal choice is to keep the cooling capacity constant when you lower the size of thecompressor and motor and increase the heat exchangers. People buy an appliance on the basis of itscooling capacity, not its electrical consumption! However, one manufacturer reported that theindustry’s choice would be to share 50/50 the overcapacity generated, in order to keep the samecompressor. A conservative estimate was used for the undercost: 20% of variable cost only incompressor cost while it can reach 50% for large performance steps but may be nil for smallchanges remaining in the same ‘frame’.

In the same way manufacturers and traders are not to request the same relative margin (as

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percentage) for higher-value goods as for lower-value goods; hence a possible marginal value of20% instead of a regular 40% regular margin. The combination of the two favourable assumptionsgives the lower value of the overcost range that a consumer may encounter.

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Table 7.9 Overcosts for model B

Singleoptions

Definition Manufact.overcost

EERincrease

New New Downsundercost

Consumerovercost

(No.) (EURO) For option EER Pe (EURO) (EURO)

1b Frontal areaHE

46.5 0.08 2.60 2.02 3.8 51/65

2b Depth coilHE

36 0.16 2.82 1.86 8.4 33/50

5 HE Findesign

2 0.11 2.67 1.96 7.2 –6/3

6 HE Tubedesign

4 0.08 2.62 2.00 4.8 –1/6

8b COMP. Effic. 35 0.05 2.55 2.06 2.2 39/49

9 Alt refriger 100 0.1 2.67 1.96 0 120/140

10 Inverter 47 0.10 2.55 2.06 0 56-66

The manufacturing cost increases are assumed to be passed completely to consumers through priceincreases. Two levels of price were assumed: a 40% (base-case) and a 20% (lower value) mark-upover manufacturing cost increases, to include distribution and sales costs. The averagemanufacturing mark-up is 30%; thus a 40% total mark-up implies a 10% mark-up for distributionand sales. The lowest manufacturing mark-up is 20%, thus a total mark-up of this amount impliesthat there is no increase in mark-up for distribution and sales.

Selection of optimum package on four studied appliances (residential sector)

The optimum combination of technological options has been calculated. First the individual optionsare sorted according to the payback period (or the ratio of NPV/investment) with the higher-returnoptions first. Second the energy savings are calculated for the combined options. Finally the netpresent value (NPV) is calculated for the combined options. In order to see the impact of addingeach subsequent option, the net present value of adding a specific option is calculated. This isknown as the marginal net present value of adding a given option. Since the options are added inorder of their potential economic contribution, options are added until their marginal net presentvalue is zero or negative. This determines the optimum design and is also the point at which thetotal net present value of the combined options is maximum.

The NPV and life cycle analysis are equivalent. This is due to the fact that the life cycle cost is aconstant value minus the NPV of the improvements; thus the maximum NPV gives the minimumlife cycle cost. The constant value used in the life cycle cost is the annualized cost of the RACwithout improvements. The calculation was initially performed for the residential sector and thenextended to office, shop and hotel sectors.

EU electricity price: 0.127 EURO/kWh

Average operational time: 510 hours/year

Average RAC lifetime: 12 years for all appliances, except 10 years for SD

Annuality factor: 8.39 or 7.36 (discount rate of 6% for 12 or 10 years)

Mark-up to consumer: +40% (base-case) and +20% (lower value)

NPV is positive up to option combination (5+6+2b) for models B and C.

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Results are given here for model B:

Table 7.10 Economic optimisation of model B

Optioncombination

Costincrease(EURO)

EERincreasefor option

New EER New Pe New en.Cons.

(kWh/year)

Lowerpayback(years)

LowerNPV

(EURO)

UpperNPV

(EURO)

5 2 0.11 2.70 1.95 993 0.20 113.60 121.2

(5)+6 4 0.071 2.89 1.82 927 0.67 64.74 70.4

(5+6)+2b 36 0.131 3.27 1.61 819 3.70 64.03 79.7

(5+6+2b)+1b 46.5 0.055 3.45 1.52 777 12.00 -19.55 -6.5

(5+6+2b+1b)+8b

35 0.032 3.56 1.48 753 16.20 -23.61 -14.4

(5+6+2b+1b+8b) +10

47 0.030 3.66 1.43 731 23.59 -42.38 -30.9

(5+6+2b+1b+8b+10)+

9

100 0.057 3.87 1.36 691 27.92 -97.91 -74.0

The energy saving for options (5+6+2b), compared with the base-case annual energy consumptionof 1 102 kWh, is 277 kWh (25%) for model B. For model C, options (5+6+2b) give a saving of 82kWh (25%) compared with the base-case annual energy consumption of 327 kWh. If one movesfrom the lower NPV to the upper NPV (lower margin on overcosts, downsizing of electrical parts),the limit between cost-effective improvements and non-cost-effective ones is not altered.

A different approach to the same figures may be done in the spirit of the Kyoto Protocol. Since thecitizens of European countries are ‘buying’ CO2 emission reductions, how much can they obtainfrom new RACs at no cost (maintained LCC)? This leads to the search for the level of performanceat which the total marginal NPV is zero. For model B, it is far beyond the optimal 25%, in anuncertain zone of our study, but is around 50%.16

Sensitivity of selection

NPV calculations for other sectors were also performed, using the following values:

EU electricity price: 0.1095 EURO/kWh

Average operational times:

Sector Hotel Office Shop

Hours/year 751 815 1 026

Results for model B and model C show the same trend as in the residential sector.

The energy savings for options (5+6+2b), compared with the base-case annual energy consumption,is 408 kWh/year in hotels, 442 kWh/year in offices and 557 kWh/year in shops (about 25%) formodel B. For model C, options (5+6+2b) give a saving of 121 kWh/year in hotels, 131 kWh/year inoffices and 165 kWh/year in shops. Following are the results for model B.

16 By extrapolation of non-cost-effective energy gains, until they balance the profit generated by the cost-effective ones.

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Table 7 11: NPV analysis results for Model B – other sectors (base case)

HOTEL OFFICE SHOP

Option NPV (EURO) Payback(years)

NPV (EURO) Payback(years)

NPV (EURO) Payback(years)

5 144.99 0.16 157.58 0.15 199.10 0.12

(5)+6 83.70 0.53 91.31 0.49 116.40 0.39

(5+6)+2b 94.88 2.91 107.26 2.68 148.08 2.13

(5+6+2b)+1 -7.26 9.45 -2.34 8.71 13.91 6.92

(5+6+2b+1)+8b -16.76 12.76 -14.02 11.76 -4.96 9.34

(5+6+2b+1+8b)+10 -36.07 18.58 -33.54 17.12 -25.18 13.60

(5+6+2b+1+8b+10)+9 -86.56 21.99 -82.01 20.26 -67.00 16.10

The process was extended to two electricity price scenarios, corresponding to two future paths thatthis variable may follow. If external effects of energy are included, it means that there is a ‘societal’cost in kWh a little bit higher that the cost paid by the consumer. In other words electricity isassumed to become more expensive due to environmental pressure. This effect was studied for a20% increase, as in the ‘Renewable greenbook’ of the Comission. If competition in the electricitysector generates significant price decreases and no environmental taxation, it could lead to the othersituation: –20% on electricity cost. This was also computed as a ‘competitive’ scenario.

For model B the lower electricity prices limit the acceptable options to (5+6+2b) in all sectors. Thisis the optimum combination. Whereas with 20% higher electricity the optimum combinationchanges: for the residential sector it is the same combination of options (5+6+2b), but for the hoteland office sectors the optimum is (5+6+2b+1) and finally, for shops, with the longest operationalhours, the optimum is (5+6+2b+1+8b). The average optimum among sectors is (5+6+2b+1).

Thus 20% higher electricity prices would permit the addition of option 1 to the optimumcombination. For model C 20% lower electricity prices leave the optimum combination at (5+6+2b) in all sectorsexcept the residential sector, where adding option 2b to (5+6) results in a slightly negative NPV. Onthe other hand, with 20% higher prices the results are consistent in all sectors: the optimum being(5+6+2b). Evidently the next possible option, option 9, is quite costly for model C and even with the20% increase in electricity prices the marginal NPV is quite negative.

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Summary of economic results

The tendency is very general: the 25% improvement obtained through options (5+6+2b) is alwayscost-effective to every user. The further improvement to 36% (the technical potential) is cost-effective for some users, but not for residential ones. A graphical presentation of the results is givenbelow with two different sets of financial assumptions for the single-duct unit studied.

The figures are very similar for the two dominant types of air-cooled appliances (splits and single-ducts). The small remaining part of the market is primarily made up of multi-splits (7%), whichobviously tend to follow the pattern for splits. The study represents 89.5% of the market. Packagedunits (2.2%), which are often manufactured in the US, were subject to an LBL study similar to oursand submitted to an equivalent efficiency increase. We now only have to consider water-cooledunits (8.3%). It is widely known that it is less costly to increase the heat exchange area with water asa coolant than with air, while the other options have identical costs and benefits. The 25% cost-effective performance increase is an underestimation of the potential in that specific segment.

Figure 7.4. Example of improvements on the single-duct appliance

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BASE +25% +36% +48%

The use of inverter technology at the costs presently indicated is not cost-effective if only financialfactors are considered, disregarding the effect on comfort. Specifically, it results in a 12% energyefficiency improvement and leads to a total 48% savings potential when combined with the all otherproven technical options.

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8. POLICY ACTIONS REALISABLE BY THE YEAR 2010 8.1 Methods for the study of scenarios

The uncertainties of global market trends, relative market share etc are high for RACs because theyare a product just entering into an S-curve in growth. We made very conservative assumptions aboutall such factors. Other uncertainties arise from changes in refrigerant regulations. Economic impactson company growth patterns have been performed using an American program called USA-LBL.Special attention was paid to the impact on small and medium-sized enterprises, as well as possibleconsequences on employment, the impact on consumers, changes in sales, changes in coolingsystems, and the impact on electricity utilities. Manufacturers were interviewed and economiccalculations made on the basis of their responses. Customer phone interviews were also carried outin two countries, using a questionnaire formulated by the group members.

Change of refrigerant

It is often stated that the changes in refrigerant needed to comply with the Kyoto protocol shouldobviate the need for any improvement in the EER of RACS within that timescale. There is evidenceof the difficulty some manufacturers are finding in complying with the phasing out of R22. Butthere is also evidence pointing the other way, not just in the academic world but in the actualmarketplace. For instance, the 26 split models in the Eurovent database already using R407Cinstead of R22 display the same performance as the hundreds of other splits (2.43 compared with2.48).

In any case, a starting point should be the assumption that there will be additional costs as a result ofrefrigerant compliance in the coming years, and then it should be possible to evaluate therelationship between refrigerant and energy efficiency and how that impinges on cost.

First, the nature of the two questions is not the same: increasing energy efficiency as envisaged inthis report pays for itself. There are additional initial expenses to consumers but then benefits accrueto them later. It is not a real additional expense, given the longer view. Environmental progress maycause additional expenses to society as a whole. After the initial change, the goal is that theincreased energy efficiency should pay for itself. The present study need only check that the cost-effective measures investigated here remain cost-effective even with a change in refrigerants.

Secondly, let us note that many changes can occur at the same time in the technical world: newmaterials, new refrigerants, new lubricants, new designs, new colours etc. As soon as theintroduction of one specific change can be extended over a few years, it becomes just one of manysmall variations and its merits should be studied for themselves – hence our will to have aprogressive introduction of measures, even if they are very cost-effective. Coordination of thetiming of energy measures and environmental measures should be sought.

Thirdly, the essential point: do the changes considered here remain cost-effective with newrefrigerants (i.e. not R22)? To answer this question a simulation was repeated using the mostinteresting group of options found in Chapter 7 but using different fluids, in order to discoverwhether the manufacturers can expect to obtain similar results by using more or less the same meansas described in this study when the new fluids are compulsory.

For that purpose, the performance of the examined units was calculated using R-410a refrigerantinstead of R-22. Then the performance of the units was calculated still using R-410a but also theoptimal combination (5+6+2b). The simulation was not performed for unit C as the data regardingits compressor’s performance with the new fluid were not available. Also, it must noted that thederived results regarding the effect of using R-410a on the units’ performance might not be

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accurate. Thus, the EER change has been computed only when the technical measures were applied,as given in the following table:

Table 8.1 effect of new refrigerants on change considered in this report

UNIT EER INCREASE (WITH R-410a FLUID) (%)

A +25

B +29

D +23

Aver. +25

These results show that the percentage increase in EER is exactly the same regardless of the fluidthat is used. Thus, it can be said the proposed improvements remain just as cost-effective if analternative refrigerant is used instead of R-22.

Impacts on European companies

Manufacturers were contacted in order to gather data on current production situations and costs, aswell as their experts’ views on expected changes yielded by the introduction of product changes.Only the most promising technological improvements were submitted for the manufacturers’consideration.

Questionnaires formulated by the EERAC study partners were posted to manufacturers to obtaintheir responses. To ensure the highest possible market coverage, the questionnaires were distributedand collected with the help of the two manufacturing associations, Eurovent and CECED, who werefully supportive. As most of the information collected is considered confidential by themanufacturing industry, data are presented here in an anonymous and aggregated form.

The companies which answered the questionnaire had an overall turnover in 1997 of 721 millionEURO and an overall market share of 61.8%. The breakdown of the average unit production costs isthe following:

Machinery and other costs 12.0

Energy 1.5

Non-energy raw materials 58.0

Labour 13.5

Distribution, marketing 12.0

Royalties, know-how 3.0

TOTAL 100.0

It is important to mention that these figures are the weighted averages of the cost structures of thecompanies, which individually vary a lot: this is particularly true for the machinery costs, whichrange from 2% to 20%, and the total production costs, which range from 300 to 800 ECU.

The proposed introduction of technological innovations triggers different reactions among themanufacturers: 3 out of 5 believe that consumers will respond to these changes with indifference, asenergy efficiency considerations do not yet represent a discriminatory factor. Therefore, anyprospective price increase might result in a loss of personal market share, which will cause a partialor complete cost transfer to prices.

The majority of manufacturers believe that a higher cost will force the market to shrink and will

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inevitably induce stronger competition from aggressive and technologically advanced industriesoverseas. It is worth underlining, however, that one Japan-based manufacturer, in contrast to thiswidespread negative perception, asserts that despite a market contraction the company’s image andcompetitiveness will be positively affected by an upgrade in efficiency.

Strangely enough, when the manufacturers’ market growth forecasts are broken down by type ofunit, the figures clash somehow with the overall pessimistic view. In the case of technologicalinnovation, two manufacturers foresee a considerable increase in the number of units produced, twodo not anticipate any substantial change, while only one expects a significant decline in production.

In conclusion, the possible introduction of technological innovations seems to elicit differingresponses from the manufacturers, though they concede that most cost increases will be passed on toconsumers. Consequently, the market will shrink but its structure – on the supply side – should notundergo any major change unless the dreaded expansion of aggressive competitors from South-EastAsia and Japan occurs.

More detailed and quantitative information was given on forecast cost and structure changes as aresult of technological improvements. Perceptions of the overall effects on companies’ accounts arehardly equivocal: two manufacturers forecast an increased turnover (5% average), one expects anunchanged turnover and the other two predict a turnover decrease (ranging from 5% to 20%). On theother hand gross profits would seem to suffer more negatively: three manufacturers foresee adecrease (10–15%) while two believe there will be no change.

The effects on employment levels appear to be negative as well and there is a fear that there wouldbe a downsizing trend: three manufacturers expect lower employment (a decrease of between 5%and 20%), one manufacturer believes it will remain stable while the other manufacturer forecasts arise of between 0 and 5%.

Finally, all manufacturers appear to be sensitive to the role of energy efficiency issues in marketing,claiming that they are a key ingredient in advertising campaigns, training programmes, pricepolicies and overall corporate image.

Simulation of the effects of the technological intervention

The USA-LBL model for the appliance industry was used to evaluate the impact of the abovescenario on European manufacturers. The key input parameters included: a consumer discount rateof 6%; equity cost of capital of 4%; typical manufacturers’ mark-up of 31%; ratio of highest tolowest mark-up of 2.04; typical firm size as percentage of total shipments of 13%; industryshipment of 909 090 units; shipments by product class of 227 000; and industry income tax rate of40%. Industry price elasticity was estimated at between 20% and 28%. The other cost data wereobtained from the questionnaires sent to the manufacturers. These parameters constitute the inputdata set for the basic simulation.

The base-case company was considered to be a medium-sized company having, before thetechnological changes, 90 000 shipments, an average factory gate price of 581 EURO per unit,revenues of 50.3 million EURO, a net income of 2.91 million EURO and a return on equity (ROE)of 10.9%.

With a rather low elasticity and with substantial benefits to consumers, the unit shipments arepredicted to increase by as much as 15% in the combined option case (5+6+2b). This is the designoption with 25% energy savings. Revenues increase accordingly from 7% to 18% (around 9 millionEURO). On the other hand net income and return on equity are much more stable: the formerincreasing very slightly and the latter declining about 1%.

For the sensitivity analysis the most important design option (5+6+2b) was used as the reference.

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The input parameters and costs were modified by +20% and –20% to determine the change in theoutput variables of shipments, price, revenue and net income and ROE, always referring to the caseof design option (5+6+2b). The sensitivity analysis was also performed for the base-case and all theother individual design options; however, the results are not very different.

It is difficult to extrapolate the results obtained for one typical firm to the whole economic sector.The way the results areextrapolated (assuming that the sector is made up of a number (N) of similarfirms) is consistent with the assumption that all firms are obliged at time t (the year 2000 forinstance) to move their average EER by 25% upwards. This means that not only the average ischanged by 25% but that almost all the equipment is changed by 25%. Practically N is around 10 inthe present situation; the sector thus is represented by 10 times our typical firm.

Figure 8.1. Market transformation as predicted by the LBL model

s = 10 %σ = 10 %

+ 25 %

Presentaverage EER

Optimal EER

% Frequency

The policy option considered initially in the LBL modelling is an ideal one, and so more realisticscenarios and policy options were then used, adding more time and greater flexibility to themodelling procedure. We know that this adaptation process is highly non-linear, and the impacts ofreal scenarios and policy options on manufacturers will in fact be far smaller than are computedwith a linear interpolation, as is done here.

The overall employment picture is highly positive: in the manufacturing and trading sectors therewould be a 10% increase in number of jobs, i.e. around 600 jobs, although some job losses (or non-creation of new jobs) would occur among utilities. However, employment levels are so different inutilities than in manufacturing that this would result in a relatively limited alteration to overallnumbers (e.g. 500 jobs created instead of 600).

Methodology of the consumer survey

Consumers were interviewed in two countries, Italy and Spain, which are considered as the primarysources of demand for the European RAC market. An external company17 specialising in marketresearch carried out this part of the work in November 1998.

The interviews were based on an ad hoc questionnaire with 21 questions covering the followingmain areas of information:

• the degree of satisfaction among consumers with the various performance characteristics of

17 ASM-Analisi e Strategie di Mercato is the Italian subsidiary of the GfK group; GfK is a market research companyactive all over Europe.

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installed air-conditioning systems;• the factors motivating their purchasing decisions;• the consumer response to a new ‘improved’ product;• RAC purchasing potential in the future (short and long-term) in households without an air-

conditioning system.

In the chosen sample we tried to balance the relatively low penetration of RACs in households withthe need to ensure the statistical validity of the results from owners of air-conditioners. Therefore,samples of 2 000 (Italy) and 3 000 (Spain) households – called the ‘screening sample’ – werechosen from about 5 000 total contacts.

Through telephone interviews a ‘valid output sample’ of 300 questionnaires per country out of thetotal contacts was chosen in such a way to comprise 70% RACs owners (210 households/country)and 30% households without room air-conditioning (90 households/country). 600 validquestionnaires were finally collected.

A draft questionnaire was initially validated through 30 pilot interviews in both Italy and Spain (20households with an RAC and 10 without). These results were used to design the final questionnaire,which was then submitted to the above-mentioned ‘screening sample’. The duration of the interviewwas about 15 minutes for non-owners and 20 minutes for owners of air-conditioners.

Results of the consumer survey

The market penetration of domestic air-conditioners in Italy is approximately 10%. Of the RACsowned by the interviewed sample, 40% are fixed split and 31% of the single-duct type. On average,air-conditioning units are used for approximately 2.8 months a year and for 6 hours a day, whichconfirms the results obtained by the technical study. The overall functioning performance ofinstalled units is considered good (73% either ‘very good’ or ‘good’), and other results were alsosimilar to those found by the technical study: appliance noise (51% ‘very good’ or ‘good’) and timeneeded to reach a comfortable temperature (44% ‘very short’ or ‘short’).

Fourteen percent of the Italian owners plan to change their installed air-conditioning system, and36% of non-owners say they may want to buy one in the next few years. The RAC type they intendto buy is mostly fixed split or multi-split. The reasons behind this choice are essentially coolingperformance (45%) and a preference for a modern and technologically advanced appliance (21%).The interest in possible energy savings is quite high, with 75% of the respondents who wouldchange or buy an air-conditioning system saying they would prefer a new, improved type withconsequent savings on their electricity bill.

The penetration of domestic air-conditioners in Spain is approximately 5%. The most widespreadair-conditioning system is the fixed split (40%), followed by the packaged type (27%). On average,air-conditioning units are used for approximately 3.2 months a year and for 5 hours a day. Nearlyhalf (45%) the interviewed sample of owners had installed their RAC between 1995 and 1997. Theoverall functioning performance of installed air-conditioners is considered positive (81% ‘verygood’ or ‘good’); and the majority are happy with the noise level (65% ‘very good’ or ‘good’) andthe time needed to reach a comfortable temperature (65% ‘very short’ or ‘short’).

Sixteen percent of the Spanish owners plan to change their present system, and 19% of non- ownerssay they may want to buy a new one in the next few years. Consumers who intend to change theirair-conditioner are mostly owners of units that are more than four years old, and the overallpreference is for multi-split and fixed-split systems. The factors influencing their future choice aredifferent from those of the past, the most important being the wish to buy a modern, technologicallyadvanced system (28%) and the system’s cooling performance and price (both at 17%). The interest

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in an improved energy-saving air-conditioner is quite high (63%). The numbers of those saying theywould purchase an appliance that, even if more expensive, would guarantee savings on theelectricity bill increases with the increase in the amount of energy to be saved, but this is a non-linear trend, starting at a very low level (11.6%) and reaching a maximum of 46%.

8.2 Behavioural changes, controls, comfort conditions and thermal regulations

The behaviour of EU consumers is likely to evolve in the direction of more air-conditioning. Insome ways technical progress can allow a focus on certain improvements – better control, smallertemperature variations etc. – but this tendency is negligible when set against the overall globalgrowth in the market for RACs, which is determined by:

• the increasing demand for comfort, which is beyond our scope of control;

• the quality of buildings, whether existing or new (and the influence of thermal regulations);

• the quality of appliances, on which we can have an influence through various policy actions;

• the decisions of those involved (architects, installers etc.).

Variable speed and comfort

Better control and smaller temperature variations generally means innovations in variable poweroperation, and this trend will develop in the future. The current ‘inverter’-type models represent butthe first step in that direction and are presently sold more for their extra comfort than for theirenergy efficiency. Intermediate options exist in the form of multi-speed ventilators and compressors.Making inverters, with their lower energy consumption in the field, more attractive to the consumerwould be a clear indication of a policy in favour of progress, bringing both increased comfort andenergy efficiency. There is little evidence, however, from the manufacturers’ associations (that is,until the revision of EN 814) that even this step is being taken.

Thermal regulations

Present thermal regulations in most countries relate only to space heating. To our knowledge, onlyPortugal has developed a specific limit, which is to be applied in all building projects, on the totalcooling energy demand. An additional piece of regulation requires that central air-conditioning,instead of RACs, is to be used in buildings with more than a 25 kW cooling load. The optimisationof a building project’s space heating efficiency entails high insulation and low (although hygienic)air renewal. These tendencies are often in the direction of low air-conditioning consumption but notalways. Furthermore, optimisation of solar energy inputs is completely missing in ‘winter’ buildingcodes. There is also a large potential for the development of summer energy efficiency in buildingcodes.

Architects and installers can play an important role in the correct decision-making about air-conditioning because they advise on the match between the unit and the zone and on the importanceof good performance. Barriers to energy load reduction can be found in many countries in that thearchitect in a construction market is paid on the basis of a certain percentage of the air-conditionersinstalled, not according to square meters. They are interested in playing ‘safely’ and in siting theplant to avoid any risk of discomfort. Other types of markets, namely those expressed in terms of‘energy service’ (cooling a surface at a certain price), generate the opposite trend among the newoperators or facility managers.

Availability of data for subsidiary measures

So it is recommended that municipalities, central administrations etc. of southern European MemberStates, as well as energy agencies, consumers’ associations etc., to introduce regulations or at least

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advisory schemes on the size of systems, operating temperatures and especialy energy consumptioncalculations. All the necessary facts for establishing a common rule for the easy calculation of suchenergy consumptions have been gathered in the present study. If an ‘installed appliance’ scheme forRACs is proposed in the countries represented in this report, all the technical elements needed areavailable here. The role of maintenance has been specifically indicated as a possibility for acheivingsignificant gains.

8.3 Minimum energy efficiency standards

We have demonstrated in chapter 7 that the improvements which presently allow some RAC modelson the European market to have a better EER than others correspond to the magnitude of the gainsin cost-effectiveness for the consumer and affordability for manufacturers (25% of the rangecomputed in the study). It is not enough just to bring this information to the consumer because ofthe conditions in which he (she) makes the decision (and anyway in many cases the consumer is notthe decision-maker).

Given this, there is certainly room for the introduction of minimum efficiency standards. For theprogressive adaptation of such standards, it is necessary to establish some intermediate targets suchthat a certain percentage of existing appliances is already over the new limit, this percentage beingsufficiently distributed between countries and manufacturers. We have chosen the average of the1996 market as a suitable limit for an initial Minimum Energy Efficiency Standard (MEES) thatcould be applied in a few years (somewhere between 2000 and 2002).

Figure 8.2. First MEES (for 2000 or 2003)

% Frequency

MEES 2003= average

Optimal EER

Taking the present market average as a limit, not directly the minimum LCC value, is anintermediate step such that each producing country and each manufacturer already has satisfactoryappliances available. The average lines defined in chapter 4 and used here show slopes which arenot significant in statistical terms. For the representation of the average it is simpler to use only anEER value per class as a threshold.

One can expect a recalibration of the European market after this first MEES and a second step canbe introduced, for instance, between 2003 and 2010 at the first level +10 %.

Figure 8.3. Possible second step for MEES (2010 level is 2003 level + 10%).

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MEES 2003

Optimal EER

MEES 2010

% Frequency

Indicating both future steps in MEES is a way of creating a specific R&D effort in increasingefficiency of RACs, to which national and European funds could contribute.

First possibility: separate MEES per categories

Table 8.2.

MEES on EER First MEES (presentaverage)

Present best value Second MEES (+10%)

MS,A: Multi-split, air-cooled 2.63 3.74 2.89

PA,A: Packaged, air-cooled 2.38 2.97 2.62

PA,W: P, Water-cooled 3.32 5.42 3.55

SD,A: Single-duct, air-cooled 1.8018 3.09 2.28

SD,W: Single-duct, water-cooled 2.36 3.62 2.60

SP,A: Split, air-cooled 2.48 3.56 2.73

SP,W: Split, water-cooled 2.75 2.88 3.03

The analysis of the consequences is made laterr, after saying a few words about another possibility.

Second possibility: a global MEES with two thresholds (water, air)

Table 8.3

MEES on EER First MEES(global av.)

Categoryaverage

Present bestvalue

Second MEES(+10%)

MS,A: Multi-split, air-cooled 2.48 2.63 3.74 2.89

PA,A: Packaged, air-cooled 2.48 2.38 2.97 2.62

PA,W: Packaged, water-cooled 3.22 3.32 5.42 3.55

SD,A: Single-duct, air-cooled 2.48 2.07 3.09 2.28

SD,W: Single-duct, water-cooled 3.22 2.36 3.62 2.60

18 Due to the experimental uncertainty and to the potential existence of a size effect, the actual average of 2.07 has beenreplaced by a lower value which avoids all problems; this change, necessary in the short term due to the ‘youth’problems of EN 814, will not be necessary for longer-term measures that will take place after the results of the EUmandate to CEN on testing accuracy.

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SP,A: Split, air-cooled 2.48 2.48 3.56 2.73

SP,W: Split, water-cooled 3.22 2.75 2.88 3.03

We see immediately that this scheme is more difficult to put in practice because it has a moremarked effect on some segments of the market. We can say that this second possibility correspondsmore to the goal (energy saving) but is difficult to implement by legislation. Only the voluntarycommitment of the industry can solve the internal problems of the industry.

Discussion of consequences

With the two successive MEES levels, the percentages of models already satisfying the standards inthe most important category of RACS (splits) are as follows:

Table 8.4a. Level of performance of production from various countries.

ORIGIN OF PRODUCT Satisfying SPLITS(first MEES)

Satisfying SPLITS(second MEES)

BELGIUM 43.85% 21.93%

FRANCE 50.80% 16.04%

GREECE 62.50% 25.00%

ISRAEL 62.50% 6.25%

ITALY 65.06% 24.52%

JAPAN 61.98% 26.45%

PORTUGAL 100.00% 40.00%

SPAIN 52.38% 19.30%

TAIWAN 92.31% 69.23%

UNITED KINGDOM 22.32% 5.06%

AVERAGE 51.2% 18.8%

All categories of equipment have a good proportion of satisfactory appliances:

Table 8.4b

Category Satisfactory for 1st MEES

MS, A 46.8%

PA,A 53.7%

PA,W 52.8%

SD,A 50.0%

SD,W 23.1%

SP,A 51.6%

SP,W 50.0%

ALL 51.2%

To a large extent most manufacturers are already meeting the first MEES:

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Table 8.5. Level of performance of production from all manufacturers.

Level ofcompliance

Satisfying manufacturers

(first MEES)

Satisfying manufacturers

(second MEES)

80-100% 21.4% 0%

60-80% 23.8% 9.5%

40-60% 33.3% 7.1%

20-40% 11.9% 40.0%

0-20% 9.5% 52.4%

International comparison

The comparison has been made with the MEES and targets of goverments in the largest producingcountries. The proposed first and second MEES occur just in the middle of the lines applied bythese competitors. The first MEES is clearly needed to avoid the possibility of a number of SouthEast Asian countries, which already export a lot to Europe, being tempted to sell here the productsthat they can no longer place on their national market due to its low performance.

Figure 8.4. International comparison.

8.4 Information and labelling on appliances

Energy labelling of RACs is part of directive 75/92. It is certainly also seen as an important markettransformation tool but cannot create as significant a shift in purchasing behaviour (unless supportedby additional measures) as a strict minimum efficiency standard can. In the many situations in whichthe installer decides on the appliance, the label loses part of its effect. However, it can helpmanufacturers and consumers go further, encouraging research, promoting very efficient models etc.

1.2

1.7

2.2

2.7

3.2

0.0 2.4 2.7 3.3 3.7 4.5 5.0 5.5 6.4 7.1 7.7 10.3

Cooling capacity [kW]

EE

R

Split, cooling only, air

Split, reversible, air

Japanese targets, cooling only

Japanese targets, reversible

Korean targets, all

Korean MEES, all

China MEES, all

proposal MEES EU 2003

proposal MEES EU 2010

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(people looking for a quality indicator will be sensitive to the ‘A’ indication).

Basic features of the potential system

From a technical perspective, a number of difficult issues in the design of a room air-conditionerenergy label must be met:

(a) What product categorisation structure should be adopted and what maximum coolingcapacity threshold should be applied? How to present the categorisation to the public?

(b) How should comparative energy performance be indicated?

(c) Should only the EER be highlighted; which grading algorithms should be applied if agradings approach is adopted?

(d) How should annual energy consumption be treated?

(e) Should operating costs be supplied and if so in what form?

(f) How should other performance aspects such as cooling capacity be treated?

(g) Should part-load performance be addressed?

(h) Should heating performance also be rated for reversible units?

(i) How much information of a given complexity can the purchaser be expected to absorb?

Discussion of these questions follows from previous technical findings.

(a) Product categorisation in four technical groups (SP, MS, PA, SD) with two cooling media(air/water) gives seven types (one potential type being non-existent, MS water-cooled). Thelimit of 12 kW cooling capacity has been retained. The four technical groups should be veryclearly indicated to the public because the performance range is very different and theyshouldn’t put the best of the best category (EER=3.74) and the best of the worst category(EER=2.97) together in the same grouping. For this reason, we have prepared translations ofthe English words that could allow national consumers to understand the difference betweenproduct categories. If the consumer can differentiate them sufficiently, it’s better to makeseven categories of grading. If to the consumer these appliances are all just ‘air-conditioners’, one single grading should then be applied to them.

(b) The indication to be given on the label: the climatic influence on consumption in kWh issuch that only the EER can be used for grading within each of the seven categories; theunderstanding of EER is difficult enough, so a grading system is necessary. The EER valuewill be better understood if translated in a A-G grading system, for which the EU consumeris now ready.

(c) Which basis, EER or kWh? The translation of EER in kWh being about the same for eachtype of RAC (with two exceptions) across Europe, the A-G grading can be based on EER orkWh, so should be based on EER because it’s simpler. The two exceptions just mentionnedare: single-ducts, for which a correction could be introduced for air infiltration, but if theyremain a separate category that is clearly indicated to the consumer, this correction has noinfluence on grading; inverters, for which an improved EER compared with standard testingshould be recognised (they may be found in all categories in theory) as soon as moreexperimental evidence is available. The EER values used should be of good quality, hencethe certification logo, when available.

(d) Should we abandon indications of consumption? The difference between categories is such

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in terms of consumed kWh/m2 due to their performance that a conventional figure ofabsolute consumption calculated with our results should be also indicated on the label forpeople that can understand this indication. It would be very conventional (sizing, climate)because a better indication of energy consumption could only be national, given the widerange of equivalent numbers of hours of operation. Detailed kWh indications arerecommended for the potential ‘installed appliance’ note.

(e) Same answer as previous point (with a national and sectoral average price of electricity).

(f) Since cooling capacity is not ambiguous, it can be on the label; translation in number of m2

should remain on the additional note, with national values, because sizing the system is notan EU responsibility.

(g) Until the results of the mandate M/274 to CEN/CENELEC are available and due to the lackof technical data provided by manufacturers, it is impossible to take into account part loadperformance.

(h) Heating performance is for the time being a secondary aspect of RACs in most Europeancountries. We have shown also that there is no contradiction between performance forheating and performance for cooling; so only the indication of ‘reversible’ or ‘cooling only’need appear on the label.

(i) Other additional information that a customer may want to have is the noise level. Althoughnot compulsory it is highly recommended that this indication be given in a systematicmanner on the label (but this may be made possible by other means, e.g. voluntaryagreements).

Figure 8.5: General layout of possible label.

C o o lin g o n ly / R e v e rs ib leA ir c o o led / W a te r co o le d

S p litA /C

Ind ica tive e ne rgy consum p tionkW h /(y ea r.m ²)A c tu a l en e rgy co n su m p tio n w ill d e p e n d o nh o w th e a p p lia n ce is u se d a n d o n c lim a te

C oo ling cap ac ity [kW ]

C o o lin g o n lyA ir c o o le d

T e c h n ic a l g ro u p :S p lit, M u lt i-s p lit, W in do w ,S in g le -d u c t

E n e rg y c o n s u m p tio n :A ve ra g e n b o f h o urs * (1 0 0 W /m ²) /E E R

C o o lin g c a p a c ity :a t T 1 co n d it io n s

H e a t in g m o d e (o r n o t)C o o lin g m e d ia

A n y c e r ty fy in g lo g oE uro ve n t o r o th er

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First possibility: definition of gradings with seven separate scales

The average plots of EER/Pcooling show slopes which are not significant in statistical terms. In thecontext of the label it is recommended to use only an EER value per class as a threshold. Fordetermining the levels, some principles should first be defined.

If we assume a parallel introduction in a few years of a MEES corresponding to the average of thepresent European market, it is logical to apply a ‘G’ grading to all models under this average line.The accuracy of 6% of EN 814 and the range of practical values on the market are consistent withthe use of classes in increments of 10%.

Numerous labelling schemes which have been studied by the group support the adoption of agrading system that is based on equal 10%-wide classes. The following grading system would thenapply:

Table 8.6: Possible gradings of RACs and EER (air-cooled).

Limit (air) EER/EERav Split Multi-split Packaged Single-duct

A starts over 150 3.72 3.95 3.57 3.11

B starts over 140–150 3.47 3.68 3.33 2.90

C starts over 130–140 3.22 3.42 3.09 2.69

D starts over 120–130 2.98 3.16 2.86 2.48

E starts over 110–120 2.73 2.89 2.62 2.28

F starts over 100–10 2.48 2.63 2.38 2.07

G starts below 100 2.48 2.63 2.38 2.07

Table 8.7. Possible gradings of RACs and EER (air-cooled).

Limit (water) EER/EERav Split Packaged Single Duct

A starts over 150 4.13 4.98 3.54

B starts over 140–150 3.85 4.65 3.30

C starts over 130–140 3.58 4.32 3.07

D starts over 120–130 3.30 3.98 2.83

E starts over 110–120 3.03 3.65 2.60

F starts over 100 -110 2.75 3.32 2.36

G starts below 100 2.75 3.32 2.36

The models on the market compare in the following way with this grading:

Table 8.8

Grading (air) EER/EERav Split Multi-split Packaged Single-duct

A 150 0% 0% 0% 0%

B 140–150 0.1% 0% 0% 0%

C 130–140 1.0% 1.3% 0% 0%

D 120–130 3.6% 5.1% 3.7% 1.7%

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E 110–120 9.1% 12.0% 11.0% 31.0%

F 100 -110 34.2% 26.6% 36.6% 15.5%

G 100 52.0% 55.0% 48.8% 51.7%

Table 8.9

Grading (water) EER/EERav Split Packaged Single-duct

A 150 0% 1.4% 0%

B 140–150 0% 1.4% 7.7%

C 130–140 0% 0% 0%

D 120–130 0% 7.6% 0%

E 110–120 0% 13.9% 15.4%

F 100 -110 16.7% 26.4% 0%

G 100 83.3% 49.3% 76.9%

There is a sufficient representativity in most categories. Category D corresponds to the minimumLCC determined previously. If the gains due to variable speed are considered by the revised EN 814following the EU mandate, they bring one or two grades upwards and we have ‘A’ models in allcategories.

Second possibility: single grading of all appliances

If we start by answering that we want to have only one category called ‘air-conditioners’, thegrading scale will be different:

Table 8.10

Limit (air) EER/EERav Limit % satisfying

A starts over 150 3.72 1.1

B starts over 140–150 3.47 1.3

C starts over 130–140 3.22 2.2

D starts over 120–130 2.98 3.5

E starts over 110–120 2.73 8.6

F starts over 100–110 2.48 27.1

G starts below 100 2.48 56.2

Although easier to understand for the consumer (‘an ‘A’ appliance is an ‘A’ appliance’), this singlegrading is not very easy for the legislator because it requires different efforts from differentmanufacturers to reach a ‘A’ and results in unbalanced information on water-cooled appliances.This last problem could be avoided by limiting the benefit of European labelling to air-cooledappliances or by adding a warning on water use on water-cooled appliances. The first problem couldbe solved by a voluntary agreement among manufacturers to be ready to enforce together the newrule and develop research.

Additional measures and impacts

The impacts of the proposed labelling

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- on manufacturers

- on consumers

- on utilities

- on the environmental balance of the EU

- on CO2 emissions

- on the energy situation

are difficult to estimate as they are all effected by the vagaries of human behaviour. One cannotexpect that all consumers will change their choice from a present G/H-graded appliance to a D-classone. The label will be most effective in helping to restructure the market at the time ofimplementation of the first MEES.

8.5 Voluntary agreement of manufacturers, performance certification

Voluntary agreements should allow a low cost acceleration of the market transformation process.Any negociation of a voluntary agreement is likely to use other policy measures as a reference, forexample either the concept of a market weighted EER by a certain year or directly through anindustry enforced MEES. The weighted performance approach allows manufacturers the possibilityof sharing the burdens of research, retooling, etc between them, although a minimum performancelevel approach is easier to enforce. It's better to combine both approaches.

A voluntary agreement in principle may also aid market transformation because it can use otherinformation circuits. For instance when the final users of the equipment are not the decision makers,it is more efficient that the manufacturers oblige fitters to install products having a certainperformance level, than to expect that they would voluntarily select a more expensive but wellgraded appliance.

Possible bases for voluntary agreements in terms of MEES

Industry can reach a compromise with the Commission by removing from sale inefficientequipment, as was the case with CECED’s voluntary agreement for washing machines. If onewishes to achieve the same results as the proposed second level MEES by a voluntary agreement,the class F and G appliances (as defined in the discussion on labelling) should be removed from themarket. If one wants to achieve the fuller objective of bringing the market to its techno-economicoptimum through such an agreement, then the class D and E appliances should also be removedfrom sale. In the situation where the industry is strong enough to enforce the more challengingagreement one would also propose that a single grading of all appliances is chosen for energylabelling because of the greater clarity for the consumer. The strength of the industry commitmentwould help to solve the internal problems of technical change and allow this better solution.

Possible bases for voluntary agreements in terms of WEER

In terms of average performance, if we want to achieve by a voluntary agreement the economicoptimum (+25%) in the installed stock, the WEER (Weighted EER) at market level should change10 to 13 years before. The sooner the better; however, as it can be seen that even if the voluntaryagreement results in an immediate 100% uptake of the best technology, the target for the stockcannot be reached before 2010. As a result three scanarios have been made, having targets ofbringing the market to its optimum point by 2010, 2015 or 2020 respectively. Check points at 2005,2010, etc. would allow the Comission to monitor the progress made towards the optimum.

Table 8.11 Weighted EER corresponding to achieving the techno-economic optimum target by 2020 where

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the market shares of the various RAC types used for overall averaging are their shares in 1996.

Year 1996 2000

(=1996)

Check point

2005

Check point2010

Check point2015

Target 2020

Splits (air) 2.48 2.48 2.79 3.10 3.10 3.10

Splits (water) 2.75 2.75 3.10 3.44 3.44 3.44

Multi-splits 2.63 2.63 2.96 3.29 3.29 3.29

Packaged (water) 3.32 3.32 3.74 4.15 4.15 4.15

Packaged (air) 2.38 2.38 2.68 2.98 2.98 2.98

Single ducts (air) 2.07 2.07 2.33 2.59 2.59 2.59

Single ducts (water) 2.36 2.36 2.66 2.95 2.95 2.95

All RACs 2.44 2.44 2.75 3.06 3.06 3.06

Table 8.12 Weighted EER corresponding to achieving the techno-economic optimum target by 2015 wherethe market shares of the various RAC types used for overall averaging are their shares in 1996.

Year 1996 Check point

2000

Check point

2005

Check point2010

Target 2015

Splits (air) 2.48 2.79 3.10 3.10 3.10

Splits (water) 2.75 3.10 3.44 3.44 3.44

Multi-splits 2.63 2.96 3.29 3.29 3.29

Packaged (water) 3.32 3.74 4.15 4.15 4.15

Packaged (air) 2.38 2.68 2.98 2.98 2.98

Single ducts (air) 2.07 2.33 2.59 2.59 2.59

Single ducts (water) 2.36 2.66 2.95 2.95 2.95

All RACs 2.44 2.75 3.06 3.06 3.06

Table 8.13 Weighted EER corresponding to achieving the techno-economic optimum target by 2010 wherethe market shares of the various RAC types used for overall averaging are their shares in 1996.

Year 1996 Check point

2000

Check point

2005

Target 2010

Splits (air) 2.48 3.10 3.10 3.10

Splits (water) 2.75 3.44 3.44 3.44

Multi-splits 2.63 3.29 3.29 3.29

Packaged (water) 3.32 4.15 4.15 4.15

Packaged (air) 2.38 2.98 2.98 2.98

Single ducts (air) 2.07 2.59 2.59 2.59

Single ducts (water) 2.36 2.95 2.95 2.95

All RACs 2.44 3.06 3.06 3.06

One can judge the depth of a voluntary agreement proposed by the industry by comparing theWEER levels proposed at certain years (typically 2000 and 2005) with the WEERs of the Tables8.10 to 8.12. Voluntary agreement may cover also some additional aspects like advice on sizing,offering to only supply high performance equipment to installers, maintainance offers, indications ofacoustic power on labels, etc…

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Performance certification

Since a certification system addressing both the EER and noise is already in place for most of themarkets, there are very good prospects of having reliable performance declarations bymanufacturers. One large manufacturers’ association of Room Air Conditioners (Eurovent-Cecomaf) has built a strong commitment among its members to energy efficiency and has installed astructure that checks the performance of appliances on the market and thus increases positivecompetition on this aspect between its members. Between 80% and 90% of the EU RAC sales arefrom its members. The other association (CECED) is strongly represented among the remainingshare of EU sales although there are multiple instances of manufacturers belonging in some way toboth organisations.

Eurovent’s figures for appliances on the market have proved very useful for the present study andfor industry. CECED has a large experience in and commitment to energy efficiency and is ready tohelp in the market segment where it is representated; its data have been very useful in the segmentnot covered by Eurovent. In consequence it is clear that there are organisations with whom avoluntary agreement can be negociated and signed. The framework given by CECED under the title‘E&E’ is an example of this willingness to sign and enforce a voluntary agreement.

It has been stressed in the study that self reported values given by manufacturers can suffer fromlarger experimental errors in one market segment (Single Ducts). This segment, which has taken agrowing share of EU RAC sales, is precisely the one which is not certified in Eurovent Certification,and where measurement consistency is not realised by an adhoc business association. As aconsequence any voluntary agreement with manufacturers should in our view include:

(a) the introduction by the industry of a declared performance checking mechanism for singleduct RACs, by the same or another business association, to be created or extended on asimilar basis

(b) the consolidation by Eurovent-Certification of its performance certification scheme in thethree other segments.

Furthermore we think that the level of reliability obtained in the three RAC segments (splits, mult-splits, and single-packaged) has to be gradually realised for the “missing” segment (single ducts).The standard certification system in place under Eurovent Certification is based on systematictesting of a statistical percentage of models not on “challenge testing”. A “ challenge test ” system(checking of one manufacturer’s product at the request of another one) has been in place for anumber of years through ARI in the United States and for five years as an option at EuroventCertification. The level of hostility between companies created by a potential “challenge test”process is such that people may not report such cases when they suspect them. A statistical processis more economic and systematic, even the industry doesn’t select exactly the same process asEurovent Certification did.

8.6 – Actions by national bodies

All electric utilities can play an important role in supporting labelling schemes, although they facemarkets, which differ significantly according to legal and climatic conditions. EU Member Statescan enhance any actions initiated at the European level.

Northern Member States Utilities

For electric utilities in northern EU countries, air conditioning has emerged as an increasing marketfor which they are unlikely to need to make additional supply-side capacity (kW) investments.Provided that they can sell energy (kWh) at the correct price, air conditioners are likely to make a

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positive impact on their business while enabling consumers to enjoy increasing comfort.Nonetheless, these utilities may be bound to promote energy efficiency as part of their “publicservice” obligations, if any.

Southern Member States Utilities

For electric utilities in southern EU countries, air conditioning is a market that could pose a risk insome regions. In Summer peaking zones, additional supply side capacity investment in generation,transmission and distribution may be needed asa result of growing air conditioning loads. To knowthe extent of the phenomenon, one has to investigate the contribtion of RAC usage to the systempeak.

Table 8.14 Estimated contribution of RACs to southern utilities system peak power demand (data wasunavailable for Greece)

1996Winter peak Summer Peak

Hour GW Hour GWFrance 7 p.m. 63 11 a.m. 49Italy 6 p.m. 42 11 a.m. 40.5Portugal 11 a.m. 4.6 11 a.m. 4.2Spain 7 p.m. 24 1 p.m. 22

2020 (estimation)Winter peak Summer Peak

Hour GW Hour GWFrance 7 p.m. 105 11 a.m. 82Italy 6 p.m. 70 11 a.m. 68Portugal 11 a.m. 8 11 a.m. 7Spain 7 p.m. 40 1 p.m. 37

2020 (estimation)Contribution of RACs to system peak

Hour GWFrance 11 a.m. 0.0Italy 11 a.m. 3.5Portugal 11 a.m. 0.3Spain 1 p.m. 2.5

When the tariffs (or market prices) don’t cover the additional supply-side capacity investment, airconditioning becomes a risk for the utility because there is a disparity between the revenues and thecosts. Without entering into detail, Table 8.15 gives the estimated cost of the supply-sideinvestment, assuming a uniform capacity cost of 550 Euro/kW, needed in four Mediterraneancountries to accommodate the growth of peak load due to room air conditioners.

Table 8.15 Estimated utility capacity investments to accommodate RAC peak power demand

Additional Capacity (MW) Additional Investment

Greece 1500 825 M-Euro

Italy 3500 1925 M-Euro

Portugal 300 165 M-Euro

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Spain 2500 1375 M-Euro

TOTAL 7800 4290 M-Euro

If all users were to select the most cost-effective RACs it would save considerable investment costsfor these utilities. Such peak power investment costs are more and more difficult to recover from theconsumers and the regulators. If an economic imablance of 10 % occurs in this recovery process, itrepresents a loss of 430 Meuros, which poses a serious risk to southern utilities. When dividing bythe number of appliances sold every year (2 million during 10 years), this gives an order ofmagnitude of what some utilities could invest to avoid this load: ~21 Euro per sold appliance.

Reversibility: the new option for utilities

There is a third group of electric utilities, including EdF in France, which are not summer peakingand support the development of air conditioning. In a competitive space heating market, EdF hasbeen looking for adavantages to encourage electric space heating. EdF discovered that since summercomfort was something valued by customers, reversible air conditioners were a market opportunity.The study members think other utilities will follow, namely because space heating equipment isseldom available in the south and as soon as a RAC is available, its use in winter becomes possible.This goes beyond the scope of this study but interesting information has been gathered in annex 1 ofthe present report. On the one hand reversibility may replace less efficient electric heating sourcesbut on the other hand it may be less efficient than non-electric alternatives or lead to increased useof space heating in Southern countries. All this needs to be investigated.

Actions by Member States governments

Is there room for national measures to promote higher efficiency RACs, for European measures orfor a combination of both? Since there is a stronger climatic relationship driving RAC usage that formany other appliances, we can expect stronger national measures (to compliment Europeanmeasures) than for some other appliances. It might be appropriate to optimise RAC performance atthe national level using the tools developed in the present study.

The potential for building codes to reduce RAC related power demand if extended to addresssummertime building thermal performance in Mediterranean countries has already been mentioned.In addition to any EU labelling scheme, there is scope for national “information schemes”, namelythose addressing optimum sizing ratios and equivalent number of hours of use for energyconsumption calculations, two quantities that are better defined at the national or local level.National authorities are in a good potition to initiate training programs and/or certification schemesfor installers.

At the same time, policy measures at the EU level are necessary to give a coherent basis for nationalactions: defining objective, reliable and verifiavble efficiency categories so that these cannot appearas barriers to the internal market. Promoting energy efficiency where it is cost effective doesn’tnecessarily mean that countries with low average cooling needs shouldn’t implement givenmeasures. It is in the nature of air conditioning that households will have differing same needs fromcountry to country. If the “average” household needs 200 hours of air conditioning per year in agiven country, only households exposed to extreme climatic conditions (poor insulation, orientationto sun, lofts, …) will install air conditioning but they are likely to use it more than “average”households would do, for instance 500 h instead of 200 h. So the actual cost effectiveness of themeasures proposed may be less different from one country to the other than might otherwise bethought. This is especially true when considering that the proportion of the RAC stock used incommercial, hotel and other non-residential sectors will usually be far greater in the northern EU

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states.

These considerations could lead to the development of national RAC installation rules, as alreadydescribed in some previous EU guides on “installed appliances”. Each Member State could applythe common rules with its own climatic values. All the relevant values needed to develop policies atthe national level are available in this study. One potential example of national action is that itwould be easier to prohibit the use of drinkable water in water-cooled RACs, a costly andenvironmentally detrimental way of rejecting the heat, at the national level than at the EU level.

A specific potential exists at the national level for the improvement of maintainance schemes.Terms of reference could be defined with the national installers (and retailers) associations. The lowlevel (or complete lack) of maintainance presently evident in all countries has been taken intoaccount when computing energy consumption with a certain level of fouling. Significant energysavings may be expected from a higher level of awareness of maintainance effects. How much ofthe 20% drop in RAC efficiency due to fouling could be avoided by any given maintainance schemeand for a given cost is an interesting subject for national evaluation, prior to or independently of anycommon European measure.

8.7 – Summary of possible actions

A "first step" minimum efficiency standard is recommendable for immediate enforcement betweenyears 2000 and 2003. The proposed level is the present European average RAC performance, whichis some 25% below the cost effective optimum. Its impacts, obtained by a detailed stock simulationare given in Table 8.16

For labelling, four separate categories can be used for single-packageds, splits, multi-splits andfinally single ducts. The EER measured according to EN 814 (at the T1 conditions) is generallyrepresentative of in situ energy consumption performance. Since the ‘unit’ EER value is notrepresentative of the energy consumption for water-cooled systems, specific limits should be appliedto their apparent EER. This eventually leads us to 7 RAC categories. Single ducts have an in situperformance that is different from other RAC types, but is in proportion such that -with the presentmarket share- it doesn't seem necessary to apply a corrective term to their nominal EER to transformit into an indicator of true energy consumption. On the other hand, the positive impact of variablespeed technologies, complete 'inverters', or simply multispeed drives, that can be applied to anyclass of equipment deserves a positive correction in the rated EER; this bonus should however bedelayed until the revision of EN814 has provided an objective means of quantifying the bonus.

The impact of the labelling scheme may increase after the first step and prepare the market for thesecond level of MEES. However, the impacts of the first MEES and of labelling are not enough tomake the market reach the economic optimum. Stronger actions, such as the second MEES and theinvolvement of manufacturers, national agencies and utilities will be necessary to bring the marketcloser the optimum energy efficiency level somewhere between 2010 and 2020.

If voluntary agreements with manufacturers are used as a way to obtain better EER levels, acertification scheme similar to the one existing for splits, multi splits and single-packaged RACsshould be introduced by the manufacturers themselves for single ducts. Targets for all segmentshave been defined (over the second MEES) level, on the way to the economic optimum. Theremoval from the market of class F and G appliances can be accompanied by monitoring of theWEER, (sales-Weighted EER), for which check points have been established.

All electric utilities and agencies can have an important role. Northern utilities can promote highefficiency reversible units; see annex 1. Southern utilities could support the European schemebecause of the savings it will induce in their investments. Also, in addition to Europe-wide

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measures, southern countries could launch national information schemes on optimal sizing ratios(kW cool/m2), energy consumption indications (under the form of an equivalent number of hours ofoperation), advice on solar control and other ways to lower cooling loads can be effective to lowerRAC demand.

Aside from the +25% efficiency goal, what defines the target is the date at which this optimum isreached. The energy consumption and environmental impacts associated with various policy targetshave been estimated using the market stock model for the year 2010, the deadline for thesatisfaction of the Kyoto protocol targets and for the year 2020 and are summarised in Table 8.16.The average RAC life expectancy (10-13 years) and hence replacement rate is such that reaching thetarget in 2010 or 2015 requires almost immediate action, while targetting year 2020 to reach today’seconomic optimum would allows progressive measures.

Table 8.16 Summary of targets and scenarios

Scenario Policy measures

(labelling is anaccompanyingmeasure in all cases)

TWhsavedper yearin 2010

TWhsavedper yearin 2020

CO2saved in2010 -% of199019

CO2saved in2020M-tonnes

Annualgain inManuf.Revenue(M-Euroin 2010)

Annualconsum-erbenefit(M-Euroin 2010)

Avoidedrisk in2020(southernutilities)

BAU No measure - - - - - - -

"First Step" 1st level MEES in2003 +labelling

0.6 1.6 60% 0.7 12 72 88

"Target2020"

MEES in 2003 and2007 +labelling

2.8 8.6 120% 3.4 57 336 411

"Target2015"

MEES in 2000 and2005 +labelling

3.3 9.4 100% 3.7 67 396 485

"Target2010"

2nd level MEES in2000 +labelling

4.4 10.3 140% 4 90 528 646

High energy savings are possible, as well as significant CO2 emissions reductions, at no (in factnegative) cost, such that all parties (manufacturers, consumers and utilities) would find a benefit inthe marketing of efficient RACs. At the point of zero cost (i.e. for higher energy efficiencies thatgive the same consumer Life Cycle Cost as present) the CO2 emissions reductions would be twiceas high as those at the economic optimum, although the results are less certain for very highefficiency levels. Additional research is required to improve confidence in the analysis at higherefficiency levels.

19 Around 1 Mt CO2 emitted in 1990 due to RAC on a total of fuel related emissions of 3000 MtCO2; the percentage isexpressed in the terms of the Kyoto protocol, i.e. related to the total 1990 emissions (like the 8% target), but only theRAC emissions. In terms of the total emission the values are between 0,02 and 0,07%.

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REFERENCES

General references

EUROVENT, 1996, 1997, 1998:Eurovent Directory of Certified productsTNO, 1997: Energy labelling of room air Conditioners, Interim report for DGXVIITNO, 1998 Common final report to Contracts no. XVII/4.1031/Z/95-055 "Energy labelling of room airConditioners" and no. XVII/4.1031/Z/96-024 "Energy labelling of domestic air to air heat pumps", under the EC -SAVE programme, also financially supported by: NOVEM, the Dutch organisation for energy and environment.andNUTEK, the Swedish national board for technical development

International standards

ISO 5151:1994 ‘Non-ducted air conditioners and heat pumps – Testing and rating forperformance’

ISO 13253:1995 ‘Ducted air-conditioners and air-to-air heat pumps – Testing and rating forperformance’

European standards

The European standard EN 814-1, 2, 3 provides the basis for RAC performance results used in thisstudy (and EN-255-1, 2, 3, 4 for heating performance).

EN 814-1 (1997) ‘Air conditioners and heat pumps with electrically driven compressors –Cooling mode – Part 1: Terms, definitions and designation’

EN 814-2 (1997) ‘Air conditioners and heat pumps with electrically driven compressors –Cooling mode – Part 2: Testing and requirements for marking’

EN 814-3 (1997) ‘Air conditioners and heat pumps with electrically driven compressors –Cooling mode – Part 3: Requirements’

EN 255-1 (1997) ‘Air conditioners and heat pumps with electrically driven compressors –Heating mode – Part 1: Terms, definitions and designation’

EN 255-2 (1997) ‘Air conditioners and heat pumps with electrically driven compressors –Heating mode – Part 2: Testing and requirements for marking (space heating)

EN 255-3 (1997) ‘Air conditioners and heat pumps with electrically driven compressors –Heating mode – Part 3: Testing and requirements for marking’ (space heatingand water heating)

EN 255-4 (1997) ‘Air conditioners and heat pumps with electrically driven compressors –Heating mode – Part 4: Requirements’ (space heating and water heating)

Other standards on RAC security and sound level

IEC 60335-240(1995)‘Safety of household and similar electrical appliances – Part 2: Particularrequirements for electrical heat pumps, air-conditioners and dehumidifiers’

ISO/FDIS 13261-1 ‘Sound power rating of air-conditioning and air-source heat pump equipment– Part 1: Non-ducted’

ISO/FDIS 13261-2 ‘Sound power rating of air-conditioning and air-source heat pump equipment– Part 2: Non-ducted’

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Literature review on energy savings due to RAC inverter technology

Reference Studied modePowerKW

Energy savings

[SENS85] Experimentation heating 4.4 29 %[MILL88] Experimentation cooling/heati

ng8.8 15 - 20 %

[MACA88] Simulation heating 15 %[HORI85] Experimentation cooling/heati

ng3 15 %

[TORI87] Experimentation heating 6.9 7-15 %***[SENS89] Simulation cooling 14.5 30 %[SHIM85] Simulation heating 6.3 20 - 40 %[PARK88] Experimentation cooling 3-5 17 - 18 %***[LBNL96] cooling 10 % *****

***** = the report states that ‘a conservative value’ has been taken into account*** = gains in terms of EER (or COP) and not on energy consumption

[HORI85] 'Seasonal Efficiencies of Residential Heat Pump Air Conditioners With Inverters-DrivenCompressors', Hori M., Akamine I., Sakai T., ASHRAE Transactions 1985, pp. 1585-1595,1985

[LBNL96] 'Potential impact of alternative efficiency levels for room air', LBNL, prepared for the USDOE, 1996

[MACA88] 'Optimal comfort control for variable-speed heat pumps', MacArthur J., Grald E., ASHRAETransactions 1988 part 2, pp. 1283-1297, 1985

[MILL88] 'Laboratory Examination and Seasonal Analyses of the Dynamis Losses for a ContinuouslyVariable-Speed Heat Pump', Miller W.A., ASHRAE Transactions 1988, pp.1246-1268, 1988

[PARK88] 'The Scroll Effect', Parkes R., Refrigeration, Air Conditioning and Heat Recovery, pp.38-43,avril 1998

[SENS85] 'Annual Energy-Saving Effect of Capacity-Modulated Air Conditioner Equipped withInverter-Driven Scroll Compressor', Senshu T., Arai A., Oguni K., Harada F., ASHRAETransactions 1985 part2B, pp. 1569-1584, 1985

[SENS89] 'Research and development on packaged heat pump air-conditioners in Japan', Sensh T.,Terada H., 1988

[SHIM85] 'Inverter Control Systems in the Residential Heat Pump Air Conditioner', Shimma Y.,Tateuchi T., Sugiura H, ASHRAE Transaction, pp. 1541-1553, 1985

[TORI86] 'Prediction Using Equivalent Ratio in Estimating of the Performance of Heat Pump AirConditioner', Torikoshi K., Uemura S., Yajima R., Fujiwara M., I.I.F. - I.I.R. - CommissionsB1, B2, E1, E2, pp.233-240, 1986

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APPENDIX 1- Information on reversible air conditioners (EdF)

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Testing standards, terminologyTerminology

This terminology is in accordance with the European standard EN255-1. This standard specifies the definitions of the aircondensing and water condensing air conditioners and air to air, water to air, air to water and water to water liquidchilling packaged and heat pumps.

Heat pumps: Appliance which takes heat at a certain temperature and restores it at a higher temperature.

NOTE: When the function of the heat pump is to supply heat (to heat rooms or water for example), it is said to operatein heating mode while when its function is to take heat away (as cooling rooms for example), it is said to operate incooling mode.

Heat recovery: Use, by means of an additional heat exchanger, of the available heat provided by an appliance which ismainly controlled in cooling mode.

Inside heat exchanger: Heat exchanger designed to transfer heat to, or away from, the inside of a building or inside hotwater system (sanitary water for example).

NOTE: In the case of an air conditioning unit operating in cooling mode, this may be the evaporator, see EN 814-1.

Outside heat exchanger: Heat exchanger designed to take heat from, or transfer heat to, the outside environment, orany other available heat source.

NOTE: In the case of an air conditioning unit operating in cooling mode, this may be the condenser, see EN 814-1.

Calorific energy (QH): In heating mode, quantity of useful heat transfered by the appliance to the heat transfer fluid(see 3.14), over a defined interval of time.

NOTE: If the heat is taken from the inside exchanger for defrosting, this is appropriately taken into account.

Calorific power (PH): Calorific energy divided by the defined time interval.

Effective absorbed power (PE): Mean electrical power absorbed by the appliance over the defined time interval, andcomprising:

− the power absorbed by the compressor operation, and all power absorbed by defrosting;− the power absorbed by all the appliance's control and safety devices;− the share of the power of devices (as fans, pumps for example) ensuring the circulation of the heat transfer fluids (see

3.14) inside the appliance.

Total absorbed power (PT): Power absorbed by all the components included in the appliance when delivered.

Performance coefficient (COP): Ratio between the calorific power and the effective power absorbed by the appliance.

Operating range: Range indicated by the manufacturer and bounded by the appliance's upper and lower operatinglimits (for example: temperature, relative humidity, voltage) within which the appliance is considered to be operationaland provides specified features.

Defrosting state: In heating mode, the appliance's state corresponding to a modification or an inversion of operationwith a view to defrosting the outside heat exchanger.

Defrosting duration (tD): Duration of the appliance is in defrosting condition.

Operating cycle with defrosting: Compressor operating time between two defrosting operations, including thedefrosting duration.

Heat transfer fluid: Liquid or gas (usually water or air) used to transfer heat to or from the appliance.

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Nominal conditions: Standardized conditions used to determine the appliance's characteristic magnitudes, in particularcalorific power, absorbed power, performance coefficient.

Acoustic power level (LW): Ten times the decimal logarithm of the ratio between an acoustic power and the referenceacoustic power, expressed in decibel. The reference acoustic power is 1 pW (10-12 W).

Testing standardsInternational standardsISO 5151 (1994): « Non ducted air conditioners and heat pumps. Testing and rating for performance »ISO 13253 (1995): « Ducted air conditioners and air to air heat pumps. Testing and rating for performance »

ISO/FDIS 13256-1: « Water source heat pumps. Testing and rating for performance. Part 1: Water to air and brine to airheat pumps »ISO/FDIS 13256-2: « Water source heat pumps. Testing and rating for performance. Part 2: Water to water and brine towater heat pumps »

ANSI-ASHRAE 58 (1986): « Rating Room Air Conditioner and Packaged Terminal Air Conditioner. Heating Capacity,Method of Testing »ANSI-ASHRAE 116 (1995): Seasonal Efficiency of Unitary Air Conditioners and Heat Pumps: Methods of Testing »

European standards

EN 255-1 (1997): Air conditionners, liquid chilling packages and heat pumps with electrically driven compressors -Heating mode - Part 1: Terms, definitions and designations.

EN 255-2 (1997): Air conditionners, liquid chilling packages and heat pumps with electrically driven compressors -Heating mode - Part 2: Testing and requirements for marking for space heating units.

EN 255-3 (1997): Air conditionners, liquid chilling packages and heat pumps with electrically driven compressors -Heating mode - Part 3: Testing and requirements for marking for sanitary hot water units.

EN 255-4 (1997): Air conditionners, liquid chilling packages and heat pumps with electrically driven compressors -Heating mode - Part 4: Requirements for space heating and sanitary hot water units.

Description of standard EN 855-2

The European Standard EN 855 (1,2,3 and 4) specifies the terms, definitions and methods for the ratio and performanceof air and water cooled air conditionners, air/air and water/air heat pumps with electrically driven compressors.

Rating test conditions

Test conditions (T1) (T2) (T3) (T4)

Outside air/Water With defrost A7(6)/W50 A2(1,5)/W50 A15(12)/W50 A-7(-8)/W50*

Without defrost A7(6)/W50 A15(12)/W50 A7(6)/W35**

Exhaust air/Water A20(12)/W50 A20(12)/W35Water/Water W10/W50 W10/W35 W15/W50Water/Water B0/W50 B0/W35 B-5/W50Outside air/Recycling air With defrost A7(6)/A20(12) A2(1,5)/A20(12) A-7(-8)/A20(12)

Without defrost A7(6)/A20(12) A15(12)/A20(12)Exhaust air/recycling air A20(12)/A20(12)Exhaust air/Air A20(12)/A7(6)Outside Water/Recycling air W10/A20(12) W15/A20(12)Internal Water/Recycling air W20/A20(12)

Note 1: All air and water temperatures are inlet temperatures in °C.Note 2: All air temperatures in parentheses are wet bulb temperatures in °C.Note 3: All tests are carried out with nominal flow rates indicated by the manufacturer in m3/s. Where non nominal flowis indicated by the manufacturer, and only a range of flow rates is given, tests shall be carried out at the minimum value.

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Note 4: Permissible external pressure difference at the evaporator and condenser shall be indicated by the manufacturerin Pa for appliances with duct connection and for those discharging into double floor, double ceilling and doubleceilling. If the fan is not included, the internal pressure difference shall be indicated instead.* If (T4) is not possible, take A2(1,5)/W50** If (T3) is not possible, take A10(8)/W35

Basic principles of performance test

Measurement of the power supplied without defrosting

Stabilized operating condition for water/water and water/air appliances

This operating condition is considered to be reached and maintained when all the measured quantities remain constantwithout the set values having to be modified. Periodic fluctuations in the measured magnitudes caused by the operationof regulation and control means are permissible, provided the mean value of these fluctuations does not exceed thepermissible differences given in Table 4.

Stabilized operating condition for other appliances

To ensure that no defrosting occurs, this operating condition must be reached 2 hours before measurements begin. Thisoperating condition should be considered to be reached and maintained when all the measured magnitudes remainconstant without the set values having to be modified. Periodic fluctuations in the measured magnitudes caused by theoperation of regulation and control means are permitted, provided the mean value of these fluctuations does not exceedthe permissible differences given in Table 4.

If it is not possible to hold the stabilized condition over a period of 2 h, the power must be measured as per 4.5.3 fordefrosting appliances.

Measurement of the calorific power

To measure the power, significant magnitudes must be continuously recorded. In the case of recorders operating on acyclic basis, the sequence must be adjusted so that a complete record is performed every 2 min at least. The power mustbe measured under stabilized conditions. The measurement duration must not be less than 30 min.

Measurement of the power supplied with defrostingThe stabilized operating condition defined in 4.5.2.2 may not be reached under certain test conditions due to the outsideheat exchanger. In this case, as the operating conditions vary constantly due to the frosting up of the evaporator, all theessential values must be recorded and a corresponding mean value must be determined. In the case of automatic dataacquisition programs, all the measured values must be recorded and printed at sufficiently short intervals. After aduration of 2 h plus a defrosting cycle, the measurement must be carried out over a whole number of cycles, withoutbeing less than 2 h or greater than 24 h.

The initial period of 2 h must not be added to the 1 indicated in 4.5.2.2.

With the flow rate-volume for the heat exchanger constant, and the appliance switched on, the test conditions describedin 4.5.1 must be adjusted. The resulting inlet temperature at the inside exchanger must be held constant during theheating phase.

A change in the outlet temperature of the inside heat exchanger caused by evaporator defrosting is thereafterpermissible.

During the defrosting phase, a difference of ± 5 K in the inlet temperature of the outside exchanger is permissible over aperiod of up to 3 min, and then a difference of ± 2 K over the next 3 min. During the rest of defrosting, a difference of ±1 K in the inlet temperature of the outside exchanger and inside exchanger is permissible. When the appliance returns toheating phase, the differences stipulated above apply.

The increase in the permissible difference in the inlet temperature to ± 5 K takes account of the regulation possibilitiesof the test installation in a non stabilized operating condition. If the heat pump trips due to the overrun, the test must bedetermined using the incorporated defrosting control. The pulses of this control correspond to the starting and stopping

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points of the defrosting and heating phases.

In the case of connected assemblies or appliances, a visual check must be carried out during the test to establish whetherwater flows or not from different holes than the ones provided for this purpose.

Measurement permissible deviationsThe heating capacity shall be determined within a maximum uncertainty of 5 % independent of individual uncertaintiesmeasurement, including the uncertainty on refrigerant properties. The electrical power shall be measured within 1 %uncertainty. The uncertainty on the COP is 6 %.

Permissible differences from the set values:

Measured magnitude Permissible differences from thearithmetic mean of the values

relative to the set values

Permissible differences from theindividual measured values relative

to the set valuesWater or water containing glycol− inlet temperature ± 0.2 K ± 0.5 K− outlet temperature ± 0.3 K ± 0.6 K− flow rate (volume) ± 2 % ± 5 %− static pressure difference - ± 10 % Air − inlet temperature (dry, wet) ± 0.3 K ± 1 K− flow rate (volume) ± 2 % ± 5 %− static pressure difference - ± 10 % Voltage ± 4 % ± 4 % Marking A rating plate shall be fixed on each unit with at least the following informations (in addition to informations required bysafety standards): - Manufacturer or supplier,- Manufacturer’s model designation and serial number,- The COP of two significant figures and the test conditions at which it is measured (T1),- The heating capacity in kW, with one digit after the decimal comma but no more than tree significant figures. Performance certification When tested by Eurovent laboratory, the difference with the obtained and claimed characteristics will be less than: Air to air heat pump: Cooling capacity or heating capacity: -8% Effective power input: +8% Air to water heat pump, water to water heat pump: Cooling capacity or heating capacity: -5% Effective power input: +5%

Technical analysis Eurovent database For the reversible models, the parameters included in Eurovent database are:

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February 1, 1998 EUROVENT CertificationDirectory of Certified Products Page XX

January 31, 1999 MANUFACTURER NAME

Participant : Trade name :

Air conditioners up to 12 kW / Air cooled / Split / Reverse cycle

AC 1 / A / S / R

FLUID Outdoor Indoor

Model R XX Pc Pe (c) Ph Pe (h) MPS ducted Lw ducted Lw Mounting

Designation kW kW kW kW or not dBA or not dBA

Outdoor Indoor unit

Type : XXXXX

XXXXXXX XXXXXXX 3,20 1,04 3,20 0,95 230 - 1 - 50 N 63 N 43 L / S

XXXXXXX XXXXXXX 4,23 1,67 4,38 1,55 230 - 1 - 50 N 64 N 45 L / S

XXXXXXX XXXXXXX 5,23 2,22 5,96 2,00 230 - 1 - 50 N 67 N 51 L / S

XXXXXXX XXXXXXX 7,00 2,79 6,99 2,47 230 - 1 - 50 N 67 N 55 L / S

Pc: Total cooling capacity (kW) Pe (c): Effective power input in cooling mode (kW) Ph: Total heating capacity (kW) Pe (h): Effective power input in heating mode (kW) M.P.S.: Main Power Supply Lw dbA = A-weighted sound power level (noise) Energy Efficiency ratio Energy Efficiency Ratio is calculated as: EER (in cooling mode) = [Total cooling capacity (in kW)] / [Effective Power Input (in kW)] EER (in heating mode) = [Total heating capacity (in kW)] / [Effective Power Input (in kW)] Minimum and maximum values for EER are shown in the following tables: RAC Category EER in cooling mode EER in heating mode Min Max Average Min Max Average Multisplit 2.08 2.94 2.51 1.44 3.58 2.63 Split 1.45 3.45 2.46 1.65 3.70 2.81 For example, for a non reversible air conditioner system, the minimum and maximum values for EER are: RAC Category EER in cooling mode Min Max Average Multisplit 1.91 3.32 2.66 Split 1.59 3.25 2.40 The difference between performance in cooling mode for a non reversible and a reversible air conditioner is nosignificant. The different supplementary components of a reversible system do not infuence the global performance.

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Technical/economic analysis The optimisation at the heating mode of the split system depends on:- the climate conditions,- the heating energy need,- the cost of the split system,- the electricity price. A good optimisation reduces the electricity consumption and the global cost of the system. For these systems, we have to designed the split for all the cooling loads of air conditionning. At the heating mode, theoptimisation depends on the climate and energy needs. In the following tables, we see the optimum capacity for: - 3 locations: Trappes (near Paris), La Rochelle (Atlantic coast), Perpignan (South of France), - 3 buildings (heating energy need at Trappes): Mozart (4,7 kW), Gershwin (6 kW), Vivaldi (7 kW).

Mozart: heating energy need = 4,7 kW Heat pump

capacity at theminimum

temperature/Heating needs

40%

50%

60%

70%

80%

90%

100%

Trappes Heatingconsumption(kWh)

4960 4647 4530 4490 4480

Heating cost(Francs)

3016 2826 2754 2732 2725

Split cost (Francs) 9631 11540 13448 15357 21084

La Rochelle Heatingconsumption(kWh)

3141 2920 2798 2745 2735 2732 2732

Heatingcost(Francs)

1892 1759 1685 1653 1647 1645 1645

Split cost (Francs) 7974 9468 10963 12457 13952 15446 16941

Perpignan Heatingconsumption(kWh)

1989 1960 1943 1936 1932

Heating cost(Francs)

1163 1146 1136 1132 1130

Split cost (Francs) 11209 12744 14280 15816 17351 The grey parts of this table are the optimum overall costs including investment and operating costs during 15 years and

for this capacity, the split capacity covers the cooling loads..

Gershwin: heating energy need = 6 kW Heat pump

capacity at theminimum

temperature/Heating needs

40%

50%

60%

70%

80%

90%

100%

Trappes Heatingconsumption(kWh)

6337 5937 5786 5739 5726

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Heating cost(Francs)

3854 3610 3519 3490 3482

Split cost (Francs) 11752 14191 16630 19069 26386

La Rochelle Heatingconsumption(kWh)

3738 3583 3514 3502 3498 3497

Heating cost(Francs)

2252 2158 2116 2109 2107 2106

Split cost (Francs) 11562 13475 15389 17302 19215 21128

Perpignan Heatingconsumption(kWh)

2532 2494 2473 2463 2459

Heating cost(Francs)

1481 1459 1447 1441 1438

Split cost (Francs) 13722 15676 17630 19585 21539 The grey parts of this table are the optimum overall costs including investment and operating costs during 15 years and

for this capacity, the split capacity covers the cooling loads..

Vivaldi: heating energy need = 7 kW Heat pump

capacity at theminimum

temperature/Heating needs

40%

50%

60%

70%

80%

90%

100%

Trappes Heatingconsumption(kWh)

7358 6893 3718 6662 6647

Heating cost(Francs)

4475 4192 4085 4052 4043

Split cost (Francs) 13321 16152 18984 21815 30309

La Rochelle Heatingconsumption(kWh)

4380 4198 4117 4103 4098 4097

Heating cost(Francs)

2639 2529 2480 2471 2468 2468

Split cost (Francs) 13204 15446 17688 19930 22171 24413

Perpignan Heatingconsumption(kWh)

2936 2892 2867 2857 2851

Heating cost(Francs)

1717 1692 1677 1672 1668

Split cost (Francs) 15594 17860 20127 22393 24659 The grey parts of this table are the optimum overall costs including investment and operating costs during 15 years and

for this capacity, the split capacity covers the cooling loads.. In France, a well designed split system is as follow: - H1 part (continental part of France): the split system capacity is 50% of the heating energy need at the minimum

temperature,- H2 and H3 parts (Atlantic coast and south of France): the split system capacity is 100% of the cooling load.

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The electrical consumption for heating and cooling for an average house for three typical different French locations is(for a 138 m2 house): Consumption in kWh Trappes

(Paris) La Rochelle

(Atlantic Coast) Marignanne

(Mediterranean Coast) Heating 5570 2353 1409 Cooling 178 533 1804 The electrical consumption for cooling in Paris and in the South of France is respectively 4% and 40% of the energybill.

Conclusions From the manufacturer database analysis, we notice a no significant difference of the performance between reversibleand no reversible system. The reversible systems are economically interesting for customers. For a good installation, we must: - have a well designed system. Some recommandation guides have to specify the design and the installation. The

optimisation of the split system capacity depends on location and on energy needs,- Improve the reliability of the systems,- Improve the performance to be competitive. EDF wants a supplementary test point at the external temperature –7°C

(test with Eurovent) with a minimum COP.

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APPENDIX 2 - Additional statements of manufacturers’ associations(CECED and Eurovent/Cecomaf)