expert inquiry on innovation options for cleaner production in the chemical industry
TRANSCRIPT
Journal of Cleaner Production 11 (2003) 347–364www.cleanerproduction.net
Expert inquiry on innovation options for cleaner production in thechemical industry�
P. Eder∗
Institute for Prospective Technological Studies, WTC, Isla de la Cartuja s/n, E-41092 Seville, Spain
Received 10 June 2000; accepted 9 March 2002
Abstract
The prospects of further progress in cleaner production in the chemical industry are explored by means of an expert inquirywhich looks at the ecological and economic potentials of different technological and business innovation options as well as barriersto their development. The outcome of the inquiry is analysed with a view to identify prospective priority areas for innovationsupport policies. The analysis shows that innovation leading to alternative synthetic pathways and a shift to selling services insteadof products have especially high potentials for both strong positive ecological effects and to be important factors for competitiveness.The utilisation of these potentials depends, however, on whether different types of innovation barriers can be overcome. Suggestionsare made as to how to develop policy measures to facilitate this. 2002 Elsevier Science Ltd. All rights reserved.
Keywords: Clean technologies; Innovation; Chemical industry; Expert inquiry
1. Introduction
Innovation leading to cleaner production has a longtradition in the chemical industry, and was practised longbefore the term ‘cleaner production’ came to be in com-mon use. Eco-efficiency in the form of raw material andenergy efficiency as well as waste minimisation througha sophisticated system of coupled production1 havealways been key competitiveness-determining factorsparticularly of bulk chemical production. Many histori-cal examples of how the chemical industry has improvedenvironmental as well as economic performance by cle-aner production can be found in Refs. [1–3].
The pace of innovation is, however, slowing down inlarge parts of the chemical industry and radical inno-vation is becoming less frequent [4,5]. Especially thosesubsectors with the biggest material and energy con-
∗ Tel.:+34-95-4488-452; fax:+34-95-4488-235.E-mail address: [email protected] (P. Eder).
� This article is largely based on the IPTS technical report—EUR19055 EN, Part II B. The views expressed in this article do not neces-sarily reflect those of the European Commission.
1 Coupled production means the use of by-products of one processas raw material inputs into other processes.
0959-6526/02/$ - see front matter 2002 Elsevier Science Ltd. All rights reserved.doi:10.1016/S0959-6526(02)00060-4
sumption are in a mature state of development. Thisgives rise to the question as to how further importantimprovements in eco-efficiency can be achieved andhow a loss of competitiveness can be avoided.2
It is the aim of this article to shed light on this ques-tion. It seeks to identify the future prospects of techno-logical and business innovation that promise to bringimprovements or even breakthroughs leading to bothbetter environmental performance and competitivenessof the chemical industry, with particular reference to theEuropean situation.
The main focus of this article lies in an expert inquirythat assesses the economic and ecological potential ofa set of 36 innovation options as well as the expecteddevelopment of these options in a business-as-usual
2 Achilladelis et al. [4] show that there is a strong correlationbetween originality and market success of individual innovations, andthat a radical innovation may ultimately prove to be more profitablefor a company than an incremental innovation despite the high risksassociated with its development. This contrasts with findings that muchof the chemical industry in Europe faces fewer innovative opport-unities and diminishing returns to R & D [5]. The importance of radicalinnovation for environmental performance is, for example, stressed inRef. [6].
348 P. Eder / Journal of Cleaner Production 11 (2003) 347–364
scenario by the year 2010. Furthermore, the inquiryanalyses different potential barriers to the realisation ofthe innovation options. Based on the results of thisanalysis, a number of prospective priority areas areidentified for innovation support.
The analysis carried out in this article may be usefulfor any actor in the innovation system, comprisingresearchers and managers in academia and industry aswell as independent and knowledgeable investors [7]. Itis also of particular relevance to public policy aiming atfacilitating innovation that leads to cleaner production.
To understand the potential role of public policy, it isworth looking at those factors that are regarded as decis-ive for innovation in the sector. Achilladelis et al. [4]have analysed the most important driving forces for rad-ical innovation in the chemical industry in the period1950–1980. It turns out that the key factors were ‘ in-house expertise’ and ‘market demand’ , followed by‘science and technology advances’ and ‘ raw materials’(availability or scarcity of feedstocks). ‘Competition’came fifth and was followed by ‘governmental legis-lation’ and ‘societal needs’ .
While there is no doubt that the core responsibility ofinnovation lies with industry, there are important factorsthat can be influenced directly or indirectly by publicpolicy aiming to use the potential of innovation forenvironmental improvements. Subsidies and taxesinfluence raw material prices. Many science and tech-nology advances depend on publicly funded pre-com-petitive research. Market demand can partly be shapedthrough green public procurement and other market-based instruments of environmental policy. There is alsothe possibility of direct environmental regulationthrough government legislation. Furthermore, small andmedium-sized enterprise (SME) support programmescan help to compensate for the lack of strategic and oper-ational resources in SMEs.
Blazejczak et al. [8] pointed out that, in order to beeffective, the different policy lines need to act in combi-nation and support the different phases of innovation asa process. Furthermore, it is important to take intoaccount that the drivers of, and barriers to, innovationleading to cleaner production vary considerably betweenthe different subsectors of the chemical industry andeven between different products and processes withinone subsector [9]. Support needs, therefore, to be tunedto specific innovation options.
The inquiry and the analysis presented in this articlehave to be regarded as a first screening to initialise dis-cussions and further clarifications. Comments to theauthors or letters to the editors are especially welcomeas feedback from a broader circle of experts is essentialfor further developing the analysis.
2. Method
2.1. Approach
The expert inquiry was carried out in various stages.As a first step, a questionnaire was sent out to interrogatepotential experts in a systematic way. The results of thisprimary inquiry were evaluated and the analysis sent outagain to the respondents in a second round with a requestfor comments. Remarks were considered in a consoli-dated analysis, which was consequently discussed in anexpert workshop with representatives from academia,industry and the European Commission. Such anapproach represents a combination of the Delphi method,the critical/key technologies technique and expert panels,which are all typically used in technology foresight stud-ies. The Delphi method consists of interrogations ofexperts about a number of topics by means of successiveiterations of a given questionnaire in order to bring con-vergence of opinions and to identify clearly a possibleconsensus. The critical/key technologies approach con-sists of identifying technologies using special criteriasets against which the importance of a particular tech-nology can be measured. The use of expert panels ofsectoral and/or technological nature is common in mosttechnology foresight exercises to complement the moreformal methodologies employed for the gathering andanalysis of relevant information and knowledge, and forthe stimulation of new insights and creative views[10,11]. The chosen approach allowed the involvementof a relatively large number of experts and a systematicand multifaceted analysis as well as iterative feedbacksfrom experts in a time- and cost-efficient way.
2.2. Target group
The questionnaire was sent to 126 potential experts.‘Potential experts’ were people who had shown specialinterest in the subject of ‘sustainable chemistry’ or‘green chemistry’ by participating in a workshop organ-ised by the OECD in October 1998 [12], or because theyhad published relevant work on issues such assustainable/green chemistry, cleaner production, cleantechnologies, eco-efficiency or similar subjects.Although the inquiry aimed to develop perspectivesespecially for the European chemical industry, it wasdecided to include experts from outside Europe in theinquiry, as many important developments are under waythere. The selection of responses for analysis accordingto expertise is described in the discussion of the results.
2.3. Format
The questionnaire consisted of 13 questions on 36innovation options, which were grouped into nine categ-ories:
349P. Eder / Journal of Cleaner Production 11 (2003) 347–364
� system changes (two options);� alternative raw materials (four options);� alternative reagents (one option);� alternatives to solvents (four options);� process engineering (two options);� catalysis (four options);� separation/recycling (three options);� alternative products (11 options);� others (five options).
The innovation options were chosen and defined basedon the discussions with experts and a screening of rel-evant journals and research programmes. They were notdefined in an exclusive way; in fact, they were intention-ally overlapping in many cases. Furthermore, the expertswere asked to suggest additional innovation options andalso to answer the predefined questions for them.
2.4. The questions
The questions of the inquiry were related to four top-ics:
� ecological potential (two questions);� socioeconomic potential (three questions);� realisation by 2010 (one question);� barriers (seven types).
For the questions on the ecological potential and thesocioeconomic potential, the addressees were asked toassume that optimal framework conditions would existfor the development of innovation options, so that theirtechnological potential would be fully exploited. Thepurpose of this part of the inquiry was to get the experts’opinion on the effects of a full development of inno-vation options.
With regard to the ecological potential of the inno-vation options, the questionnaire asked experts for theiropinion on both:
� a possible increase in the technology’s ecologicalefficiency (product or function delivered per environ-mental pressure caused) through innovation; and
� the expected overall ecological effect of an innovationoption, which may be negative if the volume effectis bigger than the efficiency increase.
In order to calibrate the responses, the addresseeswere asked to consider indirect effects and to have thefollowing types of ecological impact or risk in mind:
� raw material consumption (including fossil, mineraland renewable raw materials, as well as water);
� land use;� energy consumption;� emissions to air and water;
� solid wastes;� risk/hazard by use of toxic/dangerous substances.
The questionnaire addressed three aspects related tothe socioeconomic potential:
� the expected economic importance or market size ifthe technological potential is fully utilised;
� the impact on competitiveness;� the impact on employment.
A question on realisation by 2010 was included to findout to what extent experts expect the innovation optionsto materialise under realistic conditions up to the year2010. For this, the addressees were asked to assume ascenario without important changes to the current frame-works for science and technology up to 2010 (business-as-usual).
In case the addressees did not expect a technology todevelop to its full potential by 2010, they were asked towhat extent they believed that the following factorswould be barriers to its development:
� technological feasibility;� structural/industrial/commercial barriers;� lack of research funds;� economic viability;� regulations/policy/standards;� education/skills;� lack of incentives/pressures to be environmentally fri-
endly.
Table 1 presents the exact formulation of the questionsasked on the innovation options and the possibleanswers.
3. Results
3.1. Response
In all, 72 questionnaires were completed and returned.This corresponds to a response rate of 57%. Not allrespondents answered all questions for all innovationoptions, but most respondents gave answers to a con-siderable number. The average number of answers forone of the 468 fields of the questionnaire matrix was 53;the lowest number of answers for a field was 40 and thehighest 67. Respondents came from 14 countries, ninefrom the EU and five from outside the EU (see Table 2).
The over-representation in Austria is due to good per-sonal contacts in this country, which allowed a highnumber of potential experts to be identified and guaran-teed a high response rate. The very low representationin France seems to reflect the hesitant participation ofthis country in the OECD sustainable chemistry activity,
350 P. Eder / Journal of Cleaner Production 11 (2003) 347–364
Table 1Questions and possible answers presented in the questionnaire
Questions Possible answers
Q1: Eco-efficiencyHow would the full development of the technological potential of the innovations 1=no positive effectinfluence the ecological efficiency of affected products/processes? 2=weak positive effect
3=positive effect4=strong positive effect5=radical improvement (�factor 4)
Q2: Overall ecological impactHow would the full development of the technological potential of the innovations �2=strong negative effectinfluence the overall ecological impact of the European chemical industry? �1=weak negative effect
0=no effect+1=weak positive effect+2=strong positive effect
Q3: Expected economic importance/market sizeHow would the full development of the technological potential of the innovations 1=just an anecdotal episodeinfluence the economic importance/market size of new products/processes? 2=niche demand
3=important niche demand4=market demand5=a major source of European added value
Q4: Expected impact on competitivenessHow would the full development of the technological potential of the innovations 1=no positive effectinfluence the competitiveness of Europe’s chemical industry? 2=weak positive effect
3=positive effect4=strong positive effect5=brings huge advantages
Q5: Expected impact on employmentHow would the full development of the technological potential of the innovations �2=strong negative effectinfluence employment in Europe? �1=weak negative effect
0=no effect+1=weak positive effect+2=strong positive effect
Q6: Realisation in 2010Give your opinion on realisation in 2010 1=still only an idea
2=laboratory scale3= pilot plant4=first industrial plants5=wide industrial application
BarriersIn case you do not expect a technology to develop its full potential until 2010, to 1=no barrierwhat extent do the following factors hinder its development? 2=insignificant barrier
3=barrier4=important barrier5=decisive barrier
Q7: Technological feasibilityQ8: Structural/industrial/commercial barriersQ9: Lack of research fundsQ10: Economic viabilityQ11: Regulations/policy/standardsQ12: Education/skillsQ13: Lack of incentives/pressures to be environmentally friendly
while it is above average in Italy. Generally, the numberof responses from different countries correlates more orless to the degree of participation in the OECD sus-tainable chemistry activity. To check for a possible bias,the inquiry has also been evaluated without consideringAustrian responses. It turned out that this has only minoreffects on detailed results and does not affect at all themain findings and conclusions of the inquiry. Further-
more, the answers of respondents from the United Statesand from Europe have also been analysed separately toobtain some indication of regional differences in percep-tion. Some diverging tendencies could be identified andare presented below. However, they have to be under-stood as rather anecdotal due to the low number ofrespondents from the United States.
Table 2 also reflects the occupational position of the
351P. Eder / Journal of Cleaner Production 11 (2003) 347–364
Table 2Country distribution and occupational position of respondents
Country Number of Occupational Number ofrespondents position respondents
Austria 14 Corporate strategy 12Germany 12 Marketing/business 5
managementItaly 12 Production 1
operationsNetherlands 4 Academic research 24United 4 Industrial R&D 20KingdomBelgium 3 Research 16
managementSweden 3 Other 21France 1Spain 1United States 10Japan 4Switzerland 2China 1Mexico 1
respondents. The clear majority of respondents comefrom research-related activities, and a minority from cor-porate strategy and marketing/business management.
The answers are, of course, only characteristic of thisvery group of respondents and are not representative ofany consensus of opinion on a broader level. The groupdoes, however, constitute a very interesting and relevantcommunity with respect to the subject, as it bringstogether some of the most active and renowned expertsin the field of sustainable chemistry.
3.2. Expertise
It has been shown that addressees in expert inquiriesoften respond to questions for which they have no oronly little expertise. The challenge of ensuring anacceptable level of expertise is usually met by expertauto-assessment [11]. As regards this exercise, therespondents were asked to assess their expertise for eachof the 36 innovation options. They could choose one offive categories of expertise: unfamiliar, casuallyacquainted, familiar, knowledgeable and expert. For theevaluation of the questionnaire, only those responseswere considered for which the respondents consideredthemselves to be at least familiar with the innovationoption.
Based on this criterion, 52% of all responses to indi-vidual innovation could be considered for evaluation.However, the expertise varied widely between differentinnovation options. For the option with highest expertise(closing/interlinking of material flows and recycling)76% of all responses were considered; for the optionwith lowest expertise (microwave chemistry), however,only 28% were considered.
When we look at groups of innovation options, wesee that there are four groups with relatively high expert-ise of respondents: system changes (70% familiar andhigher), process engineering (67%), alternative reagents(65%) and alternatives to solvents (64%). Expertise wasaverage for alternative raw materials (54%), and rela-tively low for alternative products (47%), others (46%),catalysis (45%) and separation (46%).
3.3. Matrix classification of innovation options
In order to analyse the opportunities for cleaner pro-duction, the individual innovation options were classifiedby simultaneously applying four main criteria:
� ecological potential;� economic potential;� expected realisation in 2010;� technological feasibility.
The resulting patterns are visualised in the innovationoptions matrix in Table 3.
The ecological potential and the economic potentialform the two dimensions of the matrix. The innovationoptions are placed in the matrix according to classi-fications of these potentials documented in Tables A1and A2 of Appendix A. (The classification for the econ-omic dimension reflects the potential economicimportant/market size. It has been found that there is astrong correlation between this parameter and theexpected competitiveness effects (see Table 4).) Thenumbers beside the denominations of the options rankthem according to their technological feasibility. Theoptions are printed red if more than 75% of qualifiedexperts see technological feasibility as a barrier,important barrier or decisive barrier. Innovation optionsare highlighted in dark blue if experts think that theywill find wide industrial application in 2010 anyway (ina business-as-usual scenario). They are highlighted inlight blue if experts believe that they will either findwide industrial application or at least be realised in firstindustrial plants. As regards the options printed in black,experts agree that they will definitely not be realised ona wide industrial scale.
As a general tendency, we see that there is quite astrong correlation between the ecological and economicpotential of the investigated innovation options. Onlyfew exceptions to this rule can be found for some tech-nologies that are economically very promising, but donot have a very big ecological potential (new drugs, newpolymers; to a lesser extent information technology andnew pesticides). Deviations from the rule are even lessimportant in the other half of the matrix, where justclosing/interlinking of material flows and recycling aswell as use of innocuous reagents seem somewhat betterecologically than economically.
352 P. Eder / Journal of Cleaner Production 11 (2003) 347–364
Table 3Innovation options matrix
Ecology category 1— Ecology category 2—Weak to Ecology category 3—Weak Ecology category 4—Strong positive effects strong positive effects positive effects No effects to weak
positive effects
Economy category 1A major source of New drugs 20European added valueEconomy category 2Market demand or Alternative synthetic Information technology 6; new New polymers 17even a major source pathways 12; pesticides 18of European added heterogeneous catalysisvalue 7; services instead of
products 1Economy category 3Market demand Solvent-free reactions; solid phase New coatings/dyes 16; new marine
reactions 30; biocatalysis 22; new antifoulants 13; new adhesives 14;solvents and cleaning agents 29; new fertilisers 15; optimisation ofnew refrigerants 26; new established processes 2; Newdetergents/surfactants 9 blowing agents 35; water instead of
organic solvents 25; improvedseparation through membranes 10;microporous catalysis 28;molecular design 34; new processtechnology 19; extended use ofwaste as raw material 24;biomimetics 33; extended use ofchromatographic separation 8
Economy category 4Important niche Closing/interlinking of material Improved separation throughdemand or even a flows and recycling 5; use of microporous systems 27; extendedmarket demand innocuous reagents 23 use of starch as feedstock 4;
extended use of cellulose asfeedstock 11; extended use oflignin as raw material 32;liquid/supercritical CO2 as solvent21; nanotechnology 36
Economic category 5Niche demand or Alternative organic solvents 3 Microwave chemistryeven an important 31niche demand
The numbers following the innovation options rank them according to their technological feasibility (1 � best, 36 � worst technological feasibility).Ranking carried out according to the number of experts who see technological feasibility as no or insignificant barrier.Red: more than 75% of thequalified experts see technological feasibility as a barrier, important barrier or decisive barrier; dark blue: in a business-as-usual scenario, theinnovation option will find wide industrial application in 2010; light blue: in a business-as-usual scenario, the innovation option will find wideindustrial application in 2010 or at least be realised in first industrial plants.
Of the investigated innovation options, there areclearly three that have an especially high potential tocontribute to sustainable development by combiningboth high ecological and economic potentials:
� alternative synthetic pathways;� heterogeneous catalysis;� services instead of products.3
3 ‘Services instead of products’ was included in the questionnaire inorder to consider developments such as servicising or offering productservices. This means that products are indispensable as a componentof a service, and not that services are provided without products, whichobviously would not make any sense in the context of the chemicalindustry.
Alternative synthetic pathways have been identified asthe most promising innovation option to improve theecological efficiency and performance of the Europeanchemical industry. They will have a strong positiveeffect if their technological potential is fully utilised.They have the potential to find a market demand or evento become a major source of European added value andwould bring a strong positive effect or even a hugeadvantage for the competitiveness of the Europeanchemical industry. Technological feasibility and econ-omic viability are above average when compared withother options. However, there are important barriers tothe development and diffusion of this innovation option(see Table 5). In a business-as-usual scenario, alternative
353P. Eder / Journal of Cleaner Production 11 (2003) 347–364
Table 4Competitiveness: ranking of innovation options with the highest per-centage of qualified respondents rating them to bring a strong positiveeffect or a huge advantage to the European chemical industry
%
1. New polymers 752. New drugs 733. Heterogeneous catalysis 704. Information technology 675. New pesticides 666. Molecular design 637. Alternative synthetic pathways 628. New fertilisers 619. New coatings/dyes 5910. Biocatalysis 5827. Extended use of waste as raw material 3328. New refrigerants 3229. Closing/interlinking of material flows and 32
recycling30. Extended use of chromatographic separation 3031. Extended use of starch as feedstock 2432. Alternative organic solvents 2433. Liquid/supercritical CO2 as solvent 2334. Extended use of cellulose as feedstock 2135. Microwave chemistry 1536. Extended use of lignin as raw material 10
Table 5Average importance of barriers: the average percentage of expertsregarding the different factors as a barrier, important barrier or decis-ive barrier
%
1. Microwave chemistry 752. Biomimetics 693. Extended use of lignin as raw material 684. Nanotechnology 655. New solvents and cleaning agents 656. Alternative synthetic pathways 657. Extended use of waste as raw material 658. Molecular design 649. Biocatalysis 6429. Alternative organic solvents 5230. Extended use of starch as feedstock 5131. Heterogeneous catalysis 4932. Services instead of products 4733. Improved separation through 45
membranes34. Extended use of chromatographic 41
separation35. Information technology 4036. Optimisation of established processes 35
synthetic pathways are foreseen to be realised only infirst industrial plants in 2010. The barriers, however, toa large extent would be susceptible to policy action. Thehighest ranked barriers experience a lack ofincentives/pressures to be environmentally friendly, alack of research funds and
structural/industrial/commercial barriers.4 Existing regu-lation and technological feasibility are the leastimportant barriers. (Quantitative data on barriers can befound in Table A3 in Appendix A.)
The ecological potential of heterogeneous catalysis isranked second highest and its market potential is compa-rable to that of alternative synthetic pathways. There isan especially high incidence of expert opinions that itcan bring a strong positive effect or a huge competitiveadvantage to the European chemical industry. In contrastto alternative synthetic pathways, heterogeneous cataly-sis is expected to find wide industrial application by2010, even in a business-as-usual scenario. Generally,barriers are seen to be relatively low.
The sale of services instead of products is the thirdinnovation option with potential for strong positiveeffects on the overall ecological impact of the Europeanchemical industry. It has about the same good marketpotential as alternative synthetic pathways and hetero-geneous catalysis. Respondents are divided about theeffect on competitiveness, but the services instead ofproducts option has the highest percentage of qualifiedrespondents rating it as having the potential to bring ahuge advantage (30%). Of all the innovation options, ithas the highest ranking as regards employment effects.Generally, barriers to its realisation are seen to be rela-tively low; technological feasibility and economicviability are not significant barriers. However, the optionis faced with important structural/industrial/commercialbarriers and with a lack of respective education/skills.In a business-as-usual scenario, it is expected that thisinnovation option will find first or even wide industrialapplication in 2010. (The current role of servicing inmanufacturing, in general, and the chemical industry, inparticular, is analysed in Ref. [14].)
The following options also seem promising from boththe ecological and economic point of view, although toa lesser extent than the three priority innovation optionsdiscussed previously: solvent-free reactions, solid phasereactions5; biocatalysis;6 new refrigerants; and newdetergents/surfactants.
New solvents and cleaning agents are seen as the pro-
4 According to Ref. [13], one important barrier to alternative tosynthetic pathways is entrenchment. Economies have developed skillsand sunk capital into particular solutions so that the cost (in terms ofrisk, time and capital) involved in moving to a fundamentally differentapproach becomes a serious deterrent. Tuning of facilitating actions toinvestment cycles is an important factor in overcoming this barrier[14].
5 This term was used in the questionnaire. As pointed out in a com-ment of an expert, it may have been more appropriate to call the inno-vation option ‘solid phase/state reactions’ .
6 Literature sees biotechnology (including biocatalysis) as the keyelement of a new technological take-off in low-mass high-value sub-sectors of the chemical industry (in particular, the pharmaceuticalindustry). See Refs. [16,17].
354 P. Eder / Journal of Cleaner Production 11 (2003) 347–364
duct group that promises most in ecological terms, butat the same time is faced with the highest barriers,especially in the fields of regulations/policy/standardsand structural/industrial/commercial barriers.
Generally, the inquiry confirms that product inno-vation is a key factor for market success and competi-tiveness. New drugs, in particular, are seen to be theinnovation option with by far the biggest potential tobecome a major source of European added value.
Furthermore, the closing/interlinking of materials andrecycling (the innovation option for which the respon-dents rated their expertise highest) is not regarded ashaving a particularly high potential for eco-efficiencyimprovements (ranking 13) and its economic importanceis rated as only average. The potential contribution toimproved competitiveness is even perceived to be lowerthan the average of all the innovation options.
Interestingly, the extended use of renewable rawmaterials (more specifically starch, cellulose or lignin)is not identified as an especially promising strategy forthe chemical industry. Experts do not see the potentialto find more than a niche demand and expect only weakpositive ecological effects.
3.4. Additional innovation options suggested byrespondents
The respondents were asked to propose additionalinnovation options to those suggested in the question-naire; 23 respondents made use of this possibility andsuggested 44 further innovation options. The suggestedoptions are quite diverse and do not present a lot of over-lap with each other. They are listed in Appendix A.
3.5. Eco-efficiency and volume effect
The analysis confirms that high eco-efficiency of anindividual option does not automatically mean a strongpositive effect on the overall ecological impact. Forexample, new marine antifoulants are ranked first foreco-efficiency but are expected to have only a low over-all positive impact. (See Table 6 for a ranking of theinnovation options according to their eco-efficiency.)This may be due to the fact that the market share ofsubstitution is expected to be low or that the volumeeffect is expected to overcompensate eco-efficiencyimprovements.
3.6. Employment effects
Regarding employment effects, the general finding isthat for almost all innovation options no effects or weakpositive effects are expected. There are only two excep-tions. Weak to strong positive effects are expected forservices instead of products, as well as for informationtechnology. While there is an expectation that increased
Table 6Eco-efficiency: ranking of innovation options with the highest percent-age of qualified respondents expecting a strong positive effect on eco-efficiency or even a radical improvement ( � factor 4)
%
1. New marine antifoulants 772. New solvents and cleaning agents 773. Solvent-free reactions, solid phase 72
reactions4. Alternative synthetic pathways 715. Services instead of products 706. New pesticides 707. New detergents/surfactants 708. Biocatalysis 709. New refrigerants 6810. Heterogeneous catalysis 6630. Extended use of cellulose as feedstock 3931. Improved separation through 39
microporous systems32. Alternative organic solvents 3333. Optimisation of established processes 3234. Extended use of lignin as raw material 2635. Extended use of chromatographic 25
separation36. Microwave chemistry 20
competitiveness through innovation can at least compen-sate possible negative employment effects resulting fromincreases in efficiency, it is clear that deeper analysis isneeded to understand better this issue.
3.7. Private business and academia
The question arises as to whether business representa-tives have other opinions about the issues of this inquirythan the respondents from academia. For this purpose,the answers of both groups of respondents have beenevaluated separately. The business group is composed ofrespondents who indicated an occupational position incorporate strategy, marketing/business management,production operations or industrial R&D (38 respondentsin all). The academia group comprises those respondentswho indicated a position in academic research (24respondents). Some of the respondents had positions inboth business and academia and were considered in bothgroups (13 respondents). Respondents who only speci-fied a position in research management or ‘other’ couldnot be considered in either group (23 respondents).
In general terms, when we look at the average of allinnovation options, business respondents turn out to besomewhat more optimistic about positive ecologicalimpacts and competitiveness effects as well as on wideindustrial application in 2010 (difference 6% of totalresponse). Academia, on the other hand, is a little moreoptimistic concerning positive employment effects;32% of business think that existingregulations/policies/standards are no barrier, while only
355P. Eder / Journal of Cleaner Production 11 (2003) 347–364
19% of academics share this attitude. A lack ofeducation/skills is seen as a higher barrier by academiathan by business. Apart from this, there are no divergingtendencies that would be valid for all or most inno-vation options.
Alternative synthetic pathways are seen in a similarway by both groups, but academia is somewhat moreoptimistic concerning realisation in 2010 (a high per-centage of business respondents expect realisation onlyin pilot plants).
Some divergence can be detected concerning the opi-nion about shifting to service offers. While academiasees it as the absolute top option with respect to positiveecological effects, business is a little less enthusiasticfrom the ecological point of view and expects weak tostrong positive effects (category 2). On the other hand,as regards realisation in 2010, academia is clearly morepessimistic than business and expects pilots rather thanwide industrial application. So, in simple language, onecould put it that academia sees a big ecological potentialbut does not expect it to be utilised, while industrybelieves that a development from products to serviceswill occur to some extent but without overwhelming eco-logical benefits. Research activities and especiallyenhanced discussion between industry and academia areneeded to clarify this issue and to understand better therelationships between eco-efficiency and a trendtowards services.
Heterogeneous catalysis is largely evaluated ident-ically by business and academia, with a small divergencewith regard to economic importance/market size poten-tial, where academia sees a clear market demand, whilebusiness tends to expect the technology to become amajor source of European added value. Within the busi-ness group, those active in corporate strategy ormarketing/business management are, however, clearlymore pessimistic about this option, especially concerningits ecological benefits.
Business expects a little more from biocatalysis thanacademia in terms of competitiveness and it sees thepotential for strong positive ecological effects while aca-demia expects weak positive effects. Also, informationtechnology is evaluated better by business than by acad-emia. In this case, business sees the potential for thetechnology to be a major source of European addedvalue and a high percentage sees the possibility of strongpositive ecological effects. This is especially true ofthose respondents from business who are active in cor-porate strategy or marketing/business management.
The lack of optimism concerning renewable rawmaterials in terms of ecological and economic effects isespecially clear among business respondents but acade-mia do not see it as an especially promising option eith-er.
Molecular design, biomimetics and new marine anti-foulants are three innovation options which are clearly
better ranked by academia than by business regardingpositive competitiveness effects.
3.8. The viewpoint of respondents from the UnitedStates
It is not possible to get statistical evidence on differentopinions of the respondents from Europe and the UnitedStates, because only 10 responses were received fromthe latter and only an average of eight responses couldbe considered for individual innovation options accord-ing to the expertise criterion. However, the group ofAmerican respondents includes some of the country’smost recognised experts in sustainable or green chemis-try and so it seems worthwhile to report some specialcharacteristics of this response population subgroup asan anecdotal indication of possible differences in percep-tion between the regions.
Compared with the European respondents, the Amer-ican respondents are more optimistic regarding both theecological and economic potential of the innovationoptions. On average, they expect that 35% of the inno-vation options will have strong positive effects on theoverall ecological impact and that 23% of the optionscan bring radical improvements in eco-efficiency(Europeans 25 and 13%). The American respondents arealso more optimistic with respect to the potential econ-omic importance/market size of the innovation options;they expect that 25% of the innovation options canbecome a major source of European added value(Europeans 19%). This contrasts to the finding that theAmerican respondents are less optimistic about realis-ation in the year 2010. On average, the Americans expectthat only 58% of the innovation options will be appliedin first industrial plants or find wide industrial appli-cation. The corresponding value is 72% for Europeanrespondents. This indicates that the American respon-dents are clearly less confident that Europe can utilisethe technological potential for innovation than the Euro-pean respondents.
While there is coincidence between American andEuropean respondents that alternative synthetic path-ways, service instead of products and heterogeneouscatalysis have the potential for strong positive effects onecological impacts, the Americans additionally see suchhigh potential for new solvents and cleaning agents; newdetergents/surfactants; the closing/interlinking ofmaterial flows and recycling; and especially for solvent-free reactions and solid phase reactions.
Regarding information technology, the Americans areless optimistic on both the potential economicimportance/market size and realisation in Europe by2010 than the Europeans. On the other hand, they clearlysee more market potential for biocatalysis, for which alleight American respondents with higher expertise expectmore than a niche demand (Europe only 56%).
356 P. Eder / Journal of Cleaner Production 11 (2003) 347–364
3.9. Check concerning expert bias
Specialists in a certain field may have a particularviewpoint. They have a very deep understanding of cer-tain aspects and so their judgment can be extremely wellfounded. On the other hand, they often tend to beespecially optimistic about the potential of this field [11].For this reason, we checked how the opinion of thoserespondents who classified themselves as experts for acertain innovation option influences the results of theanalysis. It turns out that the experts are indeed moreoptimistic than those respondents who rate themselvesas knowledgeable or casually acquainted with an inno-vation option. The percentage of experts who chose themost optimistic answer to the questions on the ecologicaland economic effects is around 10% higher than for theentire population of respondents who were considered inthe evaluation. Barriers are seen as somewhat lessimportant by experts than by the other respondents, withthe exception of education/skills, which is regarded asmore important by the experts. This sort of bias, how-ever, has only a very low impact on the results of theanalysis due to the fact that the percentage of respon-dents who rate themselves as experts for an innovationoption is low (7% of the entire population ofrespondents). If we exclude for each innovation optionthose respondents who have rated themselves as expertsfrom the evaluation, this changes the categorisation ofthe innovation options only slightly and in very fewcases. The ecological categorisation of new drugsbecomes less clear and expectations about realisation by2010 are somewhat less optimistic. Alternative syntheticpathways drop from economy category 2 to 3 (comparewith Table A2 in Appendix A), and the realisation poten-tial of nanotechnology for 2010 is seen slightly moreoptimistically. Apart from these changes, the categoris-ation is the same whether the opinion of supposedspecialists is considered or not.
4. Conclusions
The inquiry confirms that there is an important poten-tial for further progress in cleaner production in thechemical industry, in particular in Europe. It has ident-ified a number of innovation options that promise strongpositive effects on the ecological impact of this industry.These options have, at the same time, a big marketpotential and can improve considerably the competi-tiveness of European industry. However, for some of themost promising options, there are important barriers thatprevent the utilisation of their full potential if business-as-usual is continued.
Alternative synthetic pathways are an innovationoption that deserve special attention because they arevery promising in economic and ecological terms and
seem at the same time adaptable in facilitating policymeasures. More information needs to be collected on thetechnological, economic and ecological characteristics ofconcrete processes and technologies related to specificnew pathways. The very generic term used in the ques-tionnaire refers to a wide range of routes for the trans-formation of substances and materials and requiresspecification. Based on a closer definition, there shouldbe an analysis of the extent to which alternative syntheticpathways are actually emerging as new technologies andwith which diffusion environment particular cases areconfronted at the business, industry- and economy-widelevels. The relationships between pre-competitiveresearch, corporate R&D and industrial realisation ofnew pathways should be explored for them. Barriers anddrivers have to be analysed more closely, and mech-anisms should be investigated through which diffusioncan be accelerated. Comparisons between the situationsin the United States, Japan and Europe could bring aboutinteresting insights.
Heterogeneous catalysis is a technology that isalready widely used and still has considerable potentialfor further diffusion. The position of Europe in thisfield in comparison with its main competitors shouldbe clarified in order to assess the need for additionalefforts to make use of the double dividend promised bythis technology.
A number of projects have already been carried outwhich have investigated a shift from supplying servicesinstead of products in the manufacturing industry, ingeneral, and the chemical industry in particular [15,18].There is still, however, the need for a systematicappreciation of the importance of this approach withinthe structure of the European and other chemical indus-tries and of its market potential. This would be the basethat allows the development of sector-specific policyimplications. Special attention should be paid to frame-works that ensure that shifts from products to servicesare carried out in a way that allow the ecological poten-tial of this approach to be exploited in an optimal man-ner.
While the inquiry reported in this article had amedium-term view, it would be worthwhile developinga dynamic picture of innovation that also takes intoaccount long-term developments. Such an exerciseshould involve all important players in the innovationsystem, especially industry. The aim of further researchcould be to develop a vision and a technology road map(see Refs. [19,20] for an interesting example of such avision or road map) of how to approach sustainable pro-duction of substances and materials integrating differenttechnological disciplines and promising lines of inno-vation. Finally, such a process can develop into facilitat-ing mechanisms in key innovation areas for cleaner pro-duction.
357P. Eder / Journal of Cleaner Production 11 (2003) 347–364
Appendix A. List of further innovation optionssuggested by respondents (reproduction of originalwording)
100% yield by gas/solid reactions: no solvent, noworkup;100% yield by solid/solid reactions: no solvent, noworkup;Alternative energy use;Alternative source-(raw)-materials (e.g. plants,fibres, renewable resources, etc.);Approach to using CO2 soluble polymers+adhesivesto enable CO2 sol. to be used;Biomass into energy conversion;Biotechnology (genetic engineering);Carbon sequestration;Chitin/chitosan;Colours, dyes, renewables;Composites from renewable raw materials;Composites of metal and organic fibres;Direct electrochemical processes for organic andinorganic synthesis;Distributed processing-mf. at site of use;Extended use of oils+fats as raw materials;Extraction of metals;Fluorous phase and aqueous soluble homogeneouscatalysis (two-phase catalysis);Gaseous phase polymerisation;Heterogeneous catalysis in conjunction with ultra-sound or microwave activation;Homogeneous catalysis;Indirect electrochemical processes—complexes forasymmetric synthesis;
Indirect electrochemical processes—transition metalion complexes as reagents and catalysts;Indirect electrochemical processes—transition metalions as reagents in water;Intensified processes, e.g. micro-reactors intensiveconditions;Light protection, antioxidants, renewables;Metrics for environmental impact and improvementneed to be established to guide industry, regulatorsand society;Multiple cascade reactions with high yield;New innovation strategies (e.g. eco-design, eco-technology);New insulation;New management systems (e.g. learningorganisation);New process strategies (e.g. cascadic use, zero emis-sion, aquaculture);No conservation/disinfecting, renewables;Photocatalysis (hydrocarbon activation);Photovoltaic cells;Process synthesis in combination with industrialecology design methods;Risk description of processes;Risk description of products;Robotics and automation in process optimisation;Solvent-free microwave chemistry with mineraloxides or supported reagents;Sustainable agr. (combination of many conceptspractices and technologies);Systems engineering;Tools for early economic and ecological assessmentof products and processes;Use of solar energy in chemistry;Water-saving technologies.
358 P. Eder / Journal of Cleaner Production 11 (2003) 347–364
Table A1Categorisation of innovation options according to the expected effect on the overall ecological impact of Europe’s chemical industrya
Ecology category 1: strong positive effectsPercentage of experts expecting a strongpositive effect
Alternative synthetic pathways 62Heterogeneous catalysis 50Services instead of products 50Ecology category 2: weak to strong positive effects
Percentage of experts expecting a weak Percentage of experts expecting a strongpositive effect positive effect
Closing/interlinking of material flows and 52 41recyclingSolvent-free reactions, solid phase reactions 50 42Biocatalysis 49 40New solvents and cleaning agents 49 40New refrigerants 48 39New detergents/surfactants 54 38Use of innocuous reagents 48 37Ecology category 3: weak positive effectsAll innovation options not listed under categories 1, 2 or 4 belong to this categoryEcology category 4: no effects to weak positive effects
Percentage of experts expecting no effect Percentage of experts expecting a weakpositive effect
Microwave chemistry 50 45New drugs 40 30New polymers 36 41
a Assuming that the technological potential of the innovation will be fully exploited.
359P. Eder / Journal of Cleaner Production 11 (2003) 347–364
Table A2Categorisation of innovation options according to their economic importance/market size potentiala
Economy category 1: a major source of European added valuePercentage of experts expecting the option to become a major source of European added value
New drugs 47b
Economy category 2: market demand or even a major source of European added valuePercentage of experts expecting the option to Percentage of experts expecting the option tofind a market demand become a major source of European added
valueInformation technology 41 41New polymers 49 40Heterogeneous catalysis 41 38Alternative synthetic pathways 33 38New pesticides 54 35Services instead of products 45 33Economy category 3: market demand
Percentage of experts expecting the option to find a market demandNew solvents and cleaning agents 67New refrigerants 65New coatings/dyes 61New marine antifoulants 59New detergents/surfactants 58New adhesives 57New fertilisers 56Optimisation of established processes 55New blowing agents 55Water instead of organic solvents 49Improved separation through membranes 49Microporous catalysis 48Molecular design 46Extended use of waste as raw material 46New process technology 45Biomimetics 44Solvent-free reactions, solid phase reactions 43Extended use of chromatographic separation 41Biocatalysis 39Economic category 4: important niche demand or even a market demand
Percentage of experts expecting the option to Percentage of experts expecting the option tofind an important niche demand find a market demand
Improved separation through microporous 39 46systemsExtended use of starch as feedstock 38 47Closing/interlinking of material flows and 34 45recyclingExtended use of cellulose as feedstock 34 39Extended use of lignin as raw material 42 32Liquid/supercritical CO2 as solvent 37 33Use of innocuous reagents 30 37Nanotechnology 33 33Economy category 5: niche demand or even an important niche demand
Percentage of experts expecting the option to Percentage of experts expecting the option tofind a niche demand find an important niche demand
Microwave chemistry 30 30Alternative organic solventsc 35 27
a Assuming that the technological potential of the innovation options is fully exploited.b The consensus of expert opinion is relatively low for this innovation option. Theclassification can therefore be tentative only.c Experts are divided on this innovation option: 29% see the chance to find a market demand.
360 P. Eder / Journal of Cleaner Production 11 (2003) 347–364T
able
A3
Popu
latio
nof
answ
ers
byqu
alifi
edre
spon
dent
sin
perc
ent
Num
ber
ofE
co-e
ffici
ency
Ove
rall
ecol
ogic
alim
pact
Eco
nom
icC
ompe
titiv
enes
sE
mpl
oym
ent
Rea
lisat
ion
in20
10re
spon
dent
sim
port
ance
/mar
ket
size
Que
stio
nnu
mbe
rQ
1Q
2Q
3Q
4Q
5Q
6
Pos
sibl
ean
swer
s(s
ee1
23
45
�2
�1
0+1
+21
23
45
12
34
5�
2�
10
+1+2
12
34
5T
able
1fo
rve
rbal
isat
ion)
1.A
ltern
ativ
esy
nthe
tic46
22
2447
242
02
3362
07
2233
382
1322
4022
07
3643
140
229
4622
path
way
s2.
Clo
sing
/in
terl
inki
ng55
013
2450
132
06
5241
09
3445
114
2342
284
27
3550
62
014
4044
ofm
ater
ial
flow
san
dre
cycl
ing
3.E
xten
ded
use
of39
513
4224
160
1124
5114
313
3439
1116
1845
165
03
4946
30
931
546
cellu
lose
asfe
edst
ock
4.E
xten
ded
use
of35
318
3238
90
924
4521
09
3847
612
1252
213
03
3658
30
626
5513
star
chas
feed
stoc
k5.
Ext
ende
dus
eof
313
2645
233
010
2753
103
1642
326
1323
556
30
357
373
426
3730
4lig
nin
asra
wm
ater
ial
6.E
xten
ded
use
of51
412
2539
202
212
5133
016
2446
144
2043
276
22
2657
132
628
3826
was
teas
raw
mat
eria
l7.
Use
ofin
nocu
ous
474
1526
4113
20
1348
370
1530
3717
722
3331
70
262
279
09
2349
19re
agen
ts8.
Solv
ent-
free
360
622
4231
03
650
423
920
4326
312
2944
120
342
486
015
4129
15re
actio
ns,
solid
phas
ere
actio
ns9.
Liq
uid/
supe
rcri
tical
474
1138
3017
04
2061
150
2237
339
730
4116
70
563
267
05
1866
11C
O2
asso
lven
t10
.W
ater
inst
ead
of52
610
3339
122
616
6116
014
2949
88
2430
344
20
6331
42
722
4326
orga
nic
solv
ents
11.
Alte
rnat
ive
orga
nic
494
2241
294
20
4250
60
3527
298
1122
4324
00
264
330
07
1445
34so
lven
ts12
.N
ewpr
oces
s44
011
3243
140
011
6127
05
2948
192
1237
3910
010
3749
53
325
4525
tech
nolo
gy13
.O
ptim
isat
ion
of53
017
5126
60
025
5125
010
2455
122
1835
3312
66
5131
60
28
2961
esta
blis
hed
proc
esse
s14
.H
eter
ogen
eous
385
524
4224
00
1634
500
814
4138
511
1451
190
940
466
00
634
59ca
taly
sis
(con
tinu
edon
next
page
)
361P. Eder / Journal of Cleaner Production 11 (2003) 347–364T
able
A3
(con
tinu
ed)
Num
ber
ofE
co-e
ffici
ency
Ove
rall
ecol
ogic
alim
pact
Eco
nom
icC
ompe
titiv
enes
sE
mpl
oym
ent
Rea
lisat
ion
in20
10re
spon
dent
sim
port
ance
/mar
ket
size
Que
stio
nnu
mbe
rQ
1Q
2Q
3Q
4Q
5Q
6
Pos
sibl
ean
swer
s(s
ee1
23
45
�2
�1
0+1
+21
23
45
12
34
5�
2�
10
+1+2
12
34
5T
able
1fo
rve
rbal
isat
ion)
15.
Mic
ropo
rous
280
739
4311
00
2146
320
1522
4815
47
4426
190
452
368
04
3939
17ca
taly
sis
16.
Bio
cata
lysi
s44
25
2345
250
012
4940
014
2039
272
1228
499
00
3853
103
1114
4627
17.
Mic
row
ave
2020
1545
200
05
5045
015
3030
1510
1530
4010
50
1168
210
029
5318
0ch
emis
try
18.
Impr
oved
390
1041
418
03
1174
133
1033
495
518
3237
80
344
448
00
947
44se
para
tion
thro
ugh
mem
bran
es19
.Im
prov
ed28
011
5032
70
022
707
47
3946
411
1130
444
00
6028
120
043
3917
sepa
ratio
nth
roug
hm
icro
poro
ussy
stem
s20
.E
xten
ded
use
of32
1322
4119
63
337
533
622
2841
313
2037
273
33
7023
00
1132
3918
chro
mat
ogra
phic
sepa
ratio
n21
.N
ewpo
lym
ers
454
2222
3120
05
3641
180
74
4940
59
1155
200
021
5326
05
1056
2922
.N
ewre
frig
eran
ts31
36
2358
100
013
4839
00
2665
103
1945
266
00
5340
70
415
4238
23.
New
blow
ing
220
1423
5014
00
1459
270
527
5514
523
3236
50
055
3214
06
1744
33ag
ents
24.
New
solv
ents
and
430
519
5819
00
1249
400
29
6721
212
3044
120
044
4412
00
1161
29cl
eani
ngag
ents
25.
New
drug
s31
1723
740
130
740
3023
03
1733
473
717
4330
03
1455
280
00
5644
26.
New
coat
ings
/dye
s36
017
2943
110
39
6424
03
1561
213
928
509
00
3658
60
323
3935
27.
New
pest
icid
es38
05
2449
220
35
5735
03
854
353
626
4026
00
3953
80
321
5324
28.
New
mar
ine
220
518
5523
00
073
270
923
599
510
4833
50
064
360
00
2653
21an
tifou
lant
s29
.N
ew41
05
2550
200
08
5438
03
1358
283
337
4513
00
3955
50
314
4439
dete
rgen
ts/s
urfa
ctan
ts30
.N
ewad
hesi
ves
300
3020
4010
03
2459
140
1017
5717
419
2641
110
052
444
04
2742
2731
.N
ewfe
rtili
sers
320
628
4422
06
963
220
016
5628
36
2948
130
038
566
03
2053
2332
.M
olec
ular
desi
gn36
614
3417
290
029
4329
06
2346
263
629
4320
00
4144
160
2332
2619
33.
Nan
otec
hnol
ogy
235
1827
3614
00
3055
150
1033
3324
019
3324
240
529
4819
032
2637
534
.In
form
atio
n39
815
2633
180
321
4433
53
1041
413
1515
4423
93
1434
400
39
2464
tech
nolo
gy35
.B
iom
imet
ics
260
1325
4221
00
2060
200
2024
4412
420
2444
80
046
468
426
4813
936
.Se
rvic
esin
stea
dof
423
1315
4525
00
1040
500
815
4533
315
2825
300
53
5141
30
2242
33pr
oduc
ts
(con
tinu
edon
next
page
)
362 P. Eder / Journal of Cleaner Production 11 (2003) 347–364T
able
A3
(con
tinu
ed)
Num
ber
ofB
arri
er:
tech
nolo
gica
lSt
ruct
ural
/indu
stri
al/
Bar
rier
:la
ckof
rese
arch
Bar
rier
:ec
onom
icB
arri
er:
regu
latio
ns/
Bar
rier
:ed
ucat
ion/
skill
sB
arri
er:
lack
ofre
spon
dent
sfe
asib
ility
com
mer
cial
barr
iers
fund
svi
abili
typo
licy/
stan
dard
sin
cent
ives
/pre
ssur
esto
been
viro
nmen
tally
frie
ndly
Que
stio
nnu
mbe
rQ
7Q
8Q
9Q
10Q
11Q
12Q
13
Pos
sibl
ean
swer
s(s
ee1
23
45
12
34
51
23
45
12
34
51
23
45
12
34
51
23
45
Tab
le1
for
verb
alis
atio
n)
1.A
ltern
ativ
esy
nthe
tic46
1435
3316
25
2633
315
520
3528
1310
2452
77
2222
3220
510
2330
2810
1020
2027
24pa
thw
ays
2.C
losi
ng/
inte
rlin
king
5523
3531
82
1132
4013
420
2742
110
1726
3021
632
1723
199
2033
2817
29
2128
2815
ofm
ater
ial
flow
san
dre
cycl
ing
3.E
xten
ded
use
of39
1733
3119
03
2937
239
634
3420
69
2326
349
3131
1714
69
3529
243
1429
2320
14ce
llulo
seas
feed
stoc
k4.
Ext
ende
dus
eof
3513
4728
130
039
3516
103
3248
133
1332
2913
1332
2923
106
750
2020
313
3532
316
star
chas
feed
stoc
k5.
Ext
ende
dus
eof
3111
1136
367
426
3033
70
2237
374
719
3726
1133
2226
117
423
5415
47
3726
1119
ligni
nas
raw
mat
eria
l6.
Ext
ende
dus
eof
5118
2041
147
721
3530
712
2741
155
1221
2429
1414
1440
239
740
2424
510
2133
2610
was
teas
raw
mat
eria
l7.
Use
ofin
nocu
ous
4715
2429
292
537
3417
78
3033
238
740
3519
031
2631
102
1034
3222
213
3330
188
reag
ents
8.So
lven
t-fr
eere
actio
ns,
369
1530
450
639
2130
36
2136
2412
1218
3330
633
2424
153
930
2721
129
2727
1818
solid
phas
ere
actio
ns9.
Liq
uid/
supe
rcri
tical
4710
3140
145
527
3927
28
3841
103
77
3932
1535
2328
133
1033
3523
013
2823
2313
CO
2as
solv
ent
10.
Wat
erin
sead
of52
1621
3326
510
3331
242
1029
3126
517
3631
107
4319
2112
512
3136
175
1726
2624
7or
gani
cso
lven
ts11
.A
ltern
ativ
eor
gani
c49
2142
2314
05
5024
210
1823
4315
310
2933
262
2525
2020
1018
3528
183
1028
3023
10so
lven
ts12
.N
ewpr
oces
s44
1329
3418
58
4431
135
832
3718
513
3437
115
3825
2013
513
2540
185
1533
2818
5te
chno
logy
13.
Opt
imis
atio
nof
5328
5020
20
2350
1411
225
3427
112
3339
177
435
2828
72
2036
2713
411
4118
237
esta
blis
hed
proc
esse
s14
.H
eter
ogen
eous
3816
3939
60
1645
2316
00
3248
163
1935
3210
334
3122
130
1533
3018
319
2231
1613
cata
lysi
s15
.M
icro
poro
us28
825
5017
04
4621
290
025
3833
48
3342
134
3232
1620
08
3823
310
2032
2416
8ca
taly
sis
16.
Bio
cata
lysi
s44
1821
2137
30
4224
268
622
5611
611
1839
1813
2418
1824
1611
2434
248
1919
3816
817
.M
icro
wav
e20
022
3339
60
3928
330
012
5329
60
639
3322
2912
476
66
656
286
1229
2918
12ch
emis
try
18.
Impr
oved
sepa
ratio
n39
1634
2822
013
4816
230
348
3810
06
2342
290
3841
173
014
3929
180
1053
2313
0th
roug
hm
embr
anes
(con
tinu
edon
next
page
)
363P. Eder / Journal of Cleaner Production 11 (2003) 347–364T
able
A3
(con
tinu
ed)
Num
ber
ofB
arri
er:
tech
nolo
gica
lSt
ruct
ural
/indu
stri
al/
Bar
rier
:la
ckof
rese
arch
Bar
rier
:ec
onom
icB
arri
er:
regu
latio
ns/
Bar
rier
:ed
ucat
ion/
skill
sB
arri
er:
lack
ofre
spon
dent
sfe
asib
ility
com
mer
cial
barr
iers
fund
svi
abili
typo
licy/
stan
dard
sin
cent
ives
/pre
ssur
esto
been
viro
nmen
tally
frie
ndly
Que
stio
nnu
mbe
rQ
7Q
8Q
9Q
10Q
11Q
12Q
13
Pos
sibl
ean
swer
s(s
ee1
23
45
12
34
51
23
45
12
34
51
23
45
12
34
51
23
45
Tab
le1
for
verb
alis
atio
n)
19.
Impr
oved
2813
2138
290
838
2921
45
3236
235
417
5029
035
3017
134
1738
2121
426
3026
134
sepa
ratio
nth
roug
hm
icro
poro
ussy
stem
s20
.E
xten
ded
use
of32
1439
2114
110
6418
144
831
4215
44
3232
257
3352
114
022
4119
190
1952
197
4ch
rom
atog
raph
icse
para
tion
21.
New
poly
mer
s45
538
4015
33
3530
285
837
2624
55
2843
188
2331
2310
135
3638
155
1323
2821
1522
.N
ewre
frig
eran
ts31
1321
548
413
3825
214
943
3017
04
1746
294
821
2521
254
4832
160
2529
2513
823
.N
ewbl
owin
g22
126
5924
06
3328
330
635
3518
66
2844
176
1616
3221
165
4726
210
2126
1621
16ag
ents
24.
New
solv
ents
and
438
2261
80
328
3928
36
3829
243
325
4719
68
2528
2811
336
4219
017
2026
2314
clea
ning
agen
ts25
.N
ewdr
ugs
3121
2121
334
1733
2917
426
1735
174
2513
3825
017
1321
2921
1624
2428
829
2921
138
26.
New
coat
ings
/dye
s36
1132
4311
414
3128
243
1139
3214
410
3434
210
2717
3317
717
4030
103
1728
2814
1427
.N
ewpe
stic
ides
389
3327
300
336
3021
96
3933
183
624
4221
69
2612
2924
933
2133
321
1518
3312
28.
New
mar
ine
2220
2545
100
040
4015
50
4530
1510
1025
5015
015
2525
1025
1520
2535
510
2525
2020
antif
oula
nts
29.
New
4115
3841
60
344
3812
36
3253
90
918
4426
311
2228
318
1736
3114
317
2026
2611
dete
rgen
ts/s
urfa
ctan
ts30
.N
ewad
hesi
ves
3012
3236
200
442
3317
48
2546
210
1224
4420
012
4428
88
1632
3612
416
2824
2012
31.
New
fert
ilise
rs32
1330
3713
70
4030
237
733
3720
310
1737
2313
2027
2020
1317
2730
207
1717
2330
1332
.M
olec
ular
desi
gn36
99
3144
63
3441
166
327
3027
139
2534
229
3913
2619
136
1641
1919
3223
3210
333
.N
anot
echn
olog
y23
016
4242
00
3737
215
526
3226
116
2228
3311
2030
3020
010
2525
355
2520
4010
534
.In
form
atio
n39
2929
2613
316
3939
60
2932
266
629
4219
100
4532
163
313
2932
1610
2929
353
3te
chno
logy
35.
Bio
mim
etic
s26
417
2946
40
2525
428
1713
1735
1717
1738
1713
1726
2217
1713
1326
3017
930
3517
936
.Se
rvic
esin
stea
dof
4244
3813
60
629
1829
1827
2724
183
2638
2112
341
1812
219
1518
3621
924
2127
189
prod
ucts
364 P. Eder / Journal of Cleaner Production 11 (2003) 347–364
References
[1] Faber M, Jost F, Muller-Furstenberger G. ‘Umweltschutz undEffizienz in der chemischen Industrie—Eine empirische Untersu-chung mit 33 Fallstudien’ , Diskussionschriften, Universitat Heid-elberg, Wirtschaftswissenschaftliche Fakultat; 1994.
[2] Porter ME, van der Linde C. Green and competitive: ending thestalemate. Harvard Business Review, September–October 1995.
[3] Christ C, editor. Production-integrated environmental protectionand waste management in the chemical industry. Wiley-VCH;Weinheim; 1999.
[4] Achilladelis B, Schwarzkopf A, Cines M. The dynamics of tech-nological innovation: the case of the chemical industry. Res Pol-icy 1990;19:1–34.
[5] Albach H, Audretsch D, Fleischer M, Greb R, Hofs E, Roller L-H, Schulz I. Innovation in the European chemical industry. Con-ference: ‘ Innovation measurement and policies’ , European Com-mission; 1997. p. 182–7. ISBN 92-828-2043-2.
[6] Weterings R, Kuijper J, Smeets E. 81 options: technology forsustainable development—Final report of the environment-ori-ented technology foresight study. Apeldoorn; 1997.
[7] Bower DJ, Keogh W. Changing patterns of innovation in a pro-cess-dominated industry. Int J Technol Manage1996;12(2):209–20.
[8] Blazejczak J, Edler D, Hemmelskamp J, Janicke M. Umweltpoli-tik und Innovation: Politikmuster und Innovationswirkungen iminternationalen Vergleich. Zeitschrift fur Umweltpolitik undUmweltrecht 1999;22(1):1–32.
[9] Clayton A, Spinardi G, Williams R. What shapes the implemen-tation of cleaner technology?—Conclusions and recommen-dations. In: Clayton A, Spinardi G, Williams R, editors. Policiesfor cleaner technology—A new agenda for government andindustry. London: Earthscan; 1999.
[10] Gavigan JP, Scapolo F. A comparison of national foresight exer-cises. Foresight 1999;1(6):491–513.
[11] Cameron H, Loveridge D, Cabrera J, Castanier L, Presmanes B,Vazquez L, van der Meulen B. Technology foresight: perspec-tives for European and international cooperation. PREST, Univer-sity of Manchester; 1996.
[12] OECD. Proceedings of the OECD workshop on sustainablechemistry, Venice,October 15–17, 1998.
[13] Clayton A, Ryan B, Williams R. Cleaner technologies and thegreening of industry: an introduction. In: Clayton A, Spinardi G,Williams R, editors. Policies for cleaner technology–A newagenda for government and industry. London: Earthscan; 1999.
[14] Duffy N, Ryan B. Fine chemicals sector. In: Clayton A, SpinardiG, Williams R, editors. Policies for cleaner technology—A newagenda for government and industry. London: Earthscan; 1999.
[15] White AL, Stoughton M, Feng L. Servicizing: the quiet transitionto extended producer responsibility. Boston: Tellus Institute,1999.
[16] Andersen B, Walsh V. Co-evolution within chemical technologysystems: a competence bloc approach. Indus Innovat2000;7(1):77–115.
[17] Miller JA. Life sciences in the chemical industry: the case forsynergy. Chem Innovat 2000;30(9):33–7.
[18] Creating eco-efficient producer service, research project fundedby the European Commission, 4th framework programme. Projectreference: ENV4980725.
[19] US Department of Energy. Plant/crop-based renewable resources2020—A vision to enhance US economic security through renew-able plant/crop-based resource use, DOE/GO-10097-385; 1998(http://www.oit.doe.gov/agriculture/).
[20] US Department of Energy. The technology road map forplant/crop-based renewable resources 2020’ , DOE/GO-10099-706; 1999 (http://www.oit.doe.gov/agriculture/).