report by the international sustainable chemistry
TRANSCRIPT
Report by the International Sustainable Chemistry Collaborative Centre for the Global Chemicals Outlook II Understanding Global and Regional Megatrends and Industry Sector Trends Relevant for Sound Chemicals Management and Opportunities in Sustainable Chemistry Innovation
Foundational Paper by the International Sustainable Chemistry Collaboration Centre for the GCO II
2 May 2018
Summary
Executive Summary 4
1 Global Megatrends
1.1 Global economic shifts 7
1.2 Technological Change 9
1.3 Impact on environment, Climate change, Resource use 13
1.4 Demographic changes 13
1.5 Urbanisation 15
1.6 Climate change and pollution 17
2 Sectoral Outlooks: Chemical Risks and Innovation Opportunities in Key Industry Sectors
2.1 The chemicals industry and the relevance of megatrends
for the chemicals management and innovation 19
2.2 Agriculture and food 20
2.2.1 Status and forecast of the sector 20
2.2.2 Potential concerns from and human health and environment perspective 20
2.2.3 Opportunities for sustainable chemistry innovation 21
2.3 Construction 22
2.3.1 Status and forecast of the sector 22
2.3.2 Potential concerns from and human health and environment perspective 23
2.3.3 Opportunities for sustainable chemistry innovation 24
2.4 Energy 24
2.4.1 Status and forecast of the sector 24
2.4.2 Potential concerns from and human health and environment perspective 26
2.4.3 Opportunities for sustainable chemistry innovation 27
2.5 Transportation / automotive 28
2.5.1 Status and forecast of the sector 28
2.5.2 Potential concerns from and human health and environment perspective 29
2.5.3 Opportunities for sustainable chemistry innovation 30
2.6 Electronics 32
2.6.1 Status and forecast of the sector 32
2.6.2 Potential concerns from and human health and environment perspective 34
2.6.3 Opportunities for sustainable chemistry innovation 35
2.7 Textiles 36
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2.7.1 Status and forecast of the sector 36
2.7.2 Potential concerns from and human health and environment perspective 38
2.7.3 Opportunities for sustainable chemistry innovation 39
2.8 Pharmaceuticals 40
2.8.1 Status and forecast of the sector 40
2.8.2 Potential concerns from and human health and environment perspective 41
2.8.3 Opportunities for sustainable chemistry innovation 43
3 List of Abbreviations 45
4 List of Figures 47
5 Bibliography 48
6 Annex I: List of Megatrends in Selected Studies 56
Foundational Paper by the International Sustainable Chemistry Collaboration Centre for the GCO II
4 May 2018
Executive Summary Chemicals are a key enabler for sustainable development and provide massive benefits to societies
(UNEP 2013a). At the same time, chemicals can cause severe harm to human health and the
environment, and thus must be managed safely (UNEP 2013b). The turnover of the chemical industry
has grown considerably over the past decades. It is expected to almost double again by 2030 compared
to 2015, when it may reach a total volume of EUR 6.3 trillion, up from EUR 3.4 trillion (US$ 7.4 trillion,
up from US$ 4 trillion). A key challenge for the coming years is to deal with the expected increase in
chemical production and use in a way that these chemicals are handled responsibly, and to foster
sustainable chemistry innovation to ensure that throughout their life-cycle, chemicals do not cause harm.
In this report, we identified six megatrends as large-scale changes which are consistently reported in
studies dealing with global socioeconomic development, technological innovation, and dynamics in the
chemical industry. These megatrends are often interacting with each other, and they are formed by, and
influencing the chemical world.
Profound global economic shifts have taken place due to the dynamic growth especially in some
emerging economies. Countries such as China and India have seen a surge in economic activity, their
growth rates outperform most developed countries and they are going to become the world’s leading
economies during this century. At the same time, a massive shift in production capacities has taken
place, and while the output of developed countries continues to increase, Asia has outperformed North
America and Europe and emerged as the uncontested leading region in terms of chemicals production.
Technological change is occurring at an increasingly fast pace. This includes the invention of new
technologies and technological equipment, but also of new processes and products, including new
chemicals. Like the production capacities, the innovation landscape has shifted as well, albeit with a
much more pronounced trend in China, which has emerged as an innovation leader and now grants
more patents on chemistry-related inventions than any other country. Other emerging economies are
showing signs of more innovative activities in chemicals-related areas, but these are considerably less
pronounced, and unlike for the shift in production capacities, developed countries are still strong on
innovation.
Resource use, scarcity and competition is a megatrend driven by increasing economic activity and
the associated material basis needed in many sectors, including the energy and chemical industry.
Overall resource use will continue to grow, and resource scarcity is expected to lead to increasing
competition between countries and between companies. Mining and fossil fuel extraction come with
considerable risks to human health and the environment, and the risks will increase with growing
demand for these resources. As products are becoming more and more sophisticated, which relates
often to more and different constituents as well as increasing mixtures at atomic or molecular level,
recollection and recycling will face increasing challenges at the same time.
Demographic changes include the growth in total population as well as the increasing life expectancy
in most countries and the associated ageing of populations. In 2017 about 7.6 billion lived in the world,
and this number is expected to increase to 8.6 billion in 2030 and 9.8 billion in 2050. While the past
decades were marked by a huge population increase in Asia, the coming decades will likely see a
comparably high increase in Africa, where by mid-century more than a quarter of the world population
is expected to live. The growing number of people will lead to growing resource demand, and as people
are moving to cities, demographic changes are closely linked with the megatrend of urbanization.
Urbanization is taking place on a historically unprecedented case. Since 2008, more people are living
in cities than in rural areas. Until 2050, an additional 2.5 billion people will move to cities and require
housing and other infrastructure, creating a massive demand in construction activities and leading to
changes in mobility and other needs, many of which need to be addressed by chemical-intensive
sectors.
Climate change and pollution is a megatrend based on large-scale environmental changes as well as
pollution problems from the local to the regional and sometimes even global level. Air, water and soil
pollution are assumed to lead to more than 9 million deaths per year, and next to their harms to human
health, pollution causes also significant economic damages. Chemical pollution is one of the
consequences of increased economic activity in emerging and developing economies, in combination
with insufficient regulation or lacking capacities to implement existing regulation in these countries.
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However, pollution is also increasing in developed countries as treatment comes more and more to its
limits and many pollutants are the results of intended use of chemicals, pharmaceuticals and other
products. Sustainability innovation can contribute to reduce greenhouse gas emissions, through
enhancing resource efficiency in the chemicals sector, but also through innovation leading to materials
and products which can drive down CO2 and other pollutant emissions in other sectors.
These megatrends are formed by, and are themselves influencing, dynamics in individual economic
sectors, with profound implications for chemical use as well as much potential for sustainable chemistry
innovation.
Agriculture and food production are already chemical-intensive operations, and their output will have
to grow considerably over the coming decades due to increasing global population and changing, more
resource-intensive diets. The global agrochemicals market had a value of US$ 215.18 billion in 2016
and is projected to grow up to US$ 250.5 billion by 2020. At the same time, biological alternatives to
synthetic or chemical fertilizers and pesticides are in increasing demand, reacting to consumers who
want food that is sustainably grown and also to stricter governmental regulations.
The global construction sector exhibits strong growth, fueled by urbanization trends in emerging and
developing economies and demand for more spacious housing and offices in developed countries. The
global market for construction chemicals is expected to grow by 9% per year and increase to more than
US$ 50 billion by 2025. Construction chemicals can cause severe harm especially to workers, and
concrete with its high CO2 emissions is a major cause of climate change. Sustainability innovation needs
to develop more benign alternatives which are safe for workers and come with reduced greenhouse gas
emissions.
The global energy sector will likely see an increase in energy demand by nearly one third until 2040.
The overall increase will lead to related growth in greenhouse gas emissions. The energy-intensive
chemical industry is expected to contribute to this growing demand, especially due to enhanced
production capacities in Asia, including China and Saudi Arabia. As with the broader economic shifts,
the largest growth of the future energy demand is projected to occur in non-OECD countries. In contrast,
efficiency gains in the European chemical industry are expected to counter-balance the increase in
production. Chemical products will play a key role in enhancing energy efficiency in other sectors, e.g.
through insulation materials, or contribute to low-carbon energy sources. Fostering these applications
can contribute significantly to the mitigation of climate change.
In the transportation and automotive sector, increasing demand for individual mobility as well as
mass-transit will lead to growing emissions of pollutants. The trend to shared mobility devices could
counteract this to some extent. A related trend enhancing sustainability of the sector is e-mobility, whose
further development requires highly advanced chemistry knowledge to manufacture batteries with higher
capacities and lower weight, volume, and costs. However, recycling of conventional car batteries is
already posing a serious health and environmental risks, and for modern e-mobility batteries,
sustainable solutions need to be developed.
The electronics sector is expected to grow from US$ 4 trillion in 2015 to US$ 4.5 trillion at the end of
2018. The use of chemicals in the manufacturing of electrical and electronic products is especially a
concern for workers. There are also high risks at the end of the life-cycle, when e-waste is often
informally scrapped for valuable material. The longevity of electronic products and their recyclability
have to be included much more strongly in the design and production phase to deal with these risks,
and hazardous substances need to be phased out or replaced by more benign chemicals. Innovative
electronic products such as light-emitting diodes (LEDs) can drive down electricity demand for the
lighting sector, and in combination with solar panels and batteries can make lighting available in less
developed off-grid regions, contributing to sustainable development.
The global textiles sector will see strong growth in the future. After the sector already doubled in the
past 15 years, overall apparel consumption is projected to increase by 63%, from 62 million tons in
2016/17 to 102 million tons in 2030. Textile production is a chemically intensive process, e.g. through
the dyeing of fibres or leather tanning as well as processing synthetic fibres. In addition, also
agrochemicals are used in cotton production. The use of chemicals in the sector has serious health
repercussions for workers in the sector and often leads to environmental damages in areas surrounding
textile factories. Solutions to improve the situation are in restricting highly hazardous chemicals e.g.
through the use of restricted substance lists, promoting substitution with more benign chemicals, and
through fostering initiatives that oppose the “fast fashion” trend.
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In the global pharmaceutical sector, global spending for medicine is projected to reach nearly $1.5
trillion by 2021, nearly US$ 370 billion higher compared to the 2016 spending level. The total volume of
medicine consumed will increase by 3% per year during the same period. The US will remain the lead
producer, followed by China. The innovation rate remains high, with an estimated 2,240 new drugs
entering the market each year until 2021. Environmental and health concerns of the sector are related
to releases of pharmaceuticals in the environment, where they can lead to detrimental effects especially
on aquatic life or contribute to antimicrobial resistance. Sustainability potential lies in designing drugs
which more readily biodegrade in the environment, but first and foremost, improvements to production
facilities are required, especially waste water management and proper use of pharmaceuticals.
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1. Global megatrends
Megatrends are “large-scale, high impact and often interdependent social, economic, political,
environmental or technological changes.” (EEA 2015: 5)1 As such, megatrends have tremendous
repercussions, including on the chemicals world. They affect the patterns of production and consumption
in economic sectors, including in the chemicals industry. They can influence the direction and pace of
innovation for new chemicals and chemical applications, and they reshape public attention and political
action on the negative impacts of hazardous substances.
It needs to be noted that there is no consensus approach about the identification of megatrends within
the literature. The notion of megatrends can be used to assess developments within just one sector like
agriculture or energy or in several interconnected sectors, in politics, the economy or the environment,
on the global, regional or national level. They are also not being conceptualized in a uniform way but
come in many varieties and shapes. For example, many reports included demographic changes as a
highly important megatrend, while others labelled demographics (as well as globalization and
technology) as a “primary force” affecting the set of megatrends (EY 2016). Causal drivers and ensuing
trends, or cause and effect can change depending on the viewpoint on these massive and interrelated
forces.
To identify the megatrends influencing global development, innovation, and the chemical industry, we
assessed 12 studies and synthesized a list of six key trends. The studies assessed are dealing with
megatrends in global development (UNDP and UNRISD 2017; UNGA 2017; National Intelligence
Council 2017; KPMG 2016; EEA 2015; Frost and Sullivan 2014), with megatrends particularly relevant
for technology and innovation (OECD 2016a; World Economic Forum 2015), and with megatrends
affecting the chemical industry (VCI 2017; Valencia 2013; Deloitte 2010. The number of megatrends we
found in the studies varied from just three (UNGA 2017) to 12 (Frost and Sullivan 2014), though there
was a clear tendency in many reports to list between six to nine megatrends.
There is scarce academic literature on megatrends, and most reports come from consultancies and
business associations, and some more from public agencies. As was done by Retief et al. (2016), we
conducted a matrix analysis to identify the megatrends which were most consistently referred to in the
literature. As the various reports used different designations for and conceptualisations of megatrends,
this analysis gives a broad indication, but still provides a relatively robust overview of megatrends
referred to elsewhere.
1 Other definitions differ, but are largely congruent with the one quoted above. See, for example, OECD 2016; UNDP and UNRISD 2017; EY 2017a; Frost and Sullivan 2014.
Foundational Paper by the International Sustainable Chemistry Collaboration Centre for the GCO II
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Table 1: Matrix analysis of megatrend studies
UNDP and UNRISD 2017
UNGA 2017
NIC 2017
KPMG 2016
EEA 2015
EY 2017a
Frost and Sullivan 2014
OECD 2016a
WEF 2015
VCI 2017
Valencia 2013
Deloitte 2010
Economic shifts - X X X X - X X - X X -
Technological change
X X X X X - - - X X - X
Resource use, scarcity and competition
- - - X X X - X - (X) X X
Demographic changes X - - X X - - X - X X -
Urbanisation - - - X X X X - - - X X
Climate change, pollution
X X X X X - - X - X X X
Health, disease, well-being
- - X - X X X X - - - X
Labor market X - - - - X - X - - - -
Interconnectivity - - - X - - X - - - - -
Consumption patterns - - - - - - - - - - - X
Individualism - - - X - - - - - - X -
Poverty and inequality
X - - - - - - - - - - -
Financing X - - - - - - - - - X -
Public debt - - - X - - - - - X - -
Conflict - - X - - - - - - - - -
Multipolarity - - - - X - - - - - - -
Mobility - - - - - - - - - - - X
Seven megatrends clearly stand across the 12 reports assessed. We are covering six of these in the
remainder of chapter 1 below. The one exception is health and well-being. Looking into the
corresponding studies, most focus on changes in the health sector, which we are covering in the sector
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analyses in chapter 2, on the impact of pollution, which we address in combination with climate change,
or on the impact on life expectancy, which we are dealing with in the section on demographic changes.
1.1. Global economic shifts
The last decades were marked by continuous economic shifts in terms of output from the US and Europe
to countries including China, India, Russia, Brazil, Indonesia, Mexico, Turkey, and to a lesser extent to
further countries in Asia, Africa, and Latin America. One aspect of these shifts is the increasing economic
size of emerging economies. Table 2 shows the world’s top 8 countries measured by gross domestic
product (GDP) both in 1990 and in 2016. The table reveals a marked shift, especially due to the vast
increase of the Chinese economy and the dynamically growing Indian market.
Table 2: Gross domestic product of the world's 10 largest economies, in constant 2010 US$.
Country Rank 1990 1990 (million) 2016 (million) Rank 2016
United States 1 9,064,413.77 16,920,327.94 1
China 11 829,561.97 9,504,208.19 2
Japan 2 4,682,813.75 6,052,671.81 3
Germany 3 2,568,633.88 3,781,698.55 4
France 4 1,907,283.79 2,810,525.38 5
United Kingdom 6 1,642,507.26 2,757,620.26 6
India 15 466,533.19 2,464,933.10 7
Brazil 8 1,192,733.08 2,248,106.28 8
Source: World Bank / data.worldbank.org
Long-term economic forecasts show a continuation of these trends. Of course, such projections come
with considerable uncertainties, which are getting larger with longer timeframes. With this caveat in
mind, it is expected that in the Asian region new “tigers” are expected to emerge (e.g. Indonesia, but
also Pakistan, Philippines, and Vietnam) next to existing lead players China and India (PwC 2017).
While the US is still the largest economy measured in nominal GDP, China has already surpassed the
US in terms of purchasing power parity (PPP), and is expected to overtake it in nominal terms around
2030. India is growing less dynamic than China but still more than the US and is thus projected to
outgrow the US by 2040 measured in PPP (PwC 2017).
It is expected that the global economy could more than double by 2050, and the seven largest emerging
economies could increase their share of global GDP from currently 35% to about 50% (PwC 2017).
Other emerging economies are likewise gaining ground, so that by 2050, six of the seven largest
economies will be emerging economies. At the same time, the EU27 is expected to lose market share
and account for less than 10% of global economic output, when it will be economically smaller than
India. Despite these dynamics, most of the G7 countries are still projected to have higher per capita
incomes than the emerging economies, but the gap will be closing.
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Table 3: Projected share of global GDP (PPPs) in 2016 and 2050.
2016 2050
China 18% 20%
India 7% 15%
US 16% 12%
EU27 15% 9%
Source: PwC 2017
A related shift is the increasing multipolarity, visible by the demise of the G7/G8 and the rise of the G20
as an extended forum for global cooperation. A further trend is the rise of non-state actors in global
governance. Civil society, or non-governmental, organizations (NGOs) have taken an increasingly
prominent role in national and international affairs (Matthews1997; Weiss et al. 2013). Multinational
corporations (MNC) have grown to vast economic size: Among the 100 largest economic entities
worldwide are 21 countries and 69 corporations (Green 2016).
Table 4: Global chemical shipments by region.
Region Shipments in 2016, in billion US$ Share of total
North America 870.1 17%
Latin America 216.0 4%
Western Europe 1,048.9 20%
Central and Eastern Europe 109.5 2%
Africa and Middle East 161.0 3%
Asia Pacific 2,792.1 54%
Total Global Shipments 5,197.6 100
American Chemistry Council 2017
The current situation in the chemicals and pharmaceuticals industry reflects these larger changes. In
the early 2000s, Asia surpassed Europe and the US as the lead market, and has since grown to become
the dominant region for the production and use of chemicals. In the Asia-Pacific region, more chemicals
are produced than in the rest of the world combined (see Table 4).
The sales forecasts for the chemical industry likewise show a continuous shift towards Asia (Roland
Berger 2015). Production capacities in the region are expanding as companies react to the growing
demand: "Rising consumer purchasing power will translate into more chemicals people can afford to
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buy, which drives the demand for chemicals across Asia" (A.T. Kearney 2012). Although the European
and US chemical industry are expected to keep growing in absolute terms, they will do so decidedly less
dynamically than the industry in the Asia-Pacific region, and thus lose a considerable amount of their
market share (see Table 5).
Table 5: Past and projected share of chemical sales across regions.
2000 2015e 2035e
Europe 33% 19% 13%
North America 27% 18% 14%
Asia 32% 53% 62%
Latin America 4% 5% 5%
Rest of world 4% 5% 6%
Source: Roland Berger 2015
1.2. Technological change
The rate of technological innovation and change is continuously increasing, and as a result, human
development has seen tremendous progress over the past decades. For the upcoming years, OECD
has put forward a set of 40 key and emerging technologies in the fields of biotechnologies, advanced
materials, energy and environment, and digitalisation (see Figure 1). Many of these technologies have
the potential to revolutionize not only their respective fields, but also aspects of human life, and thus
further increase the pace of technological change we are currently witnessing.
Technological change is not only driven by innovation, but also by society’s adoption of new
technologies on the one hand and the emergence of new ideas on the other. The adoption rate of new
technologies has increased significantly over recent decades; the smartphone is particularly
unparalleled in the pace by which it was distributed among the population (DeGusta 2012). While it took
electricity and the telephone 30 or 25 years, respectively, to be adopted by 10% of households in the
United States, the smartphone achieved this in roughly 8 years, and the tablet in 2.5 years. The next
phase of adoption, signaled by the time it took shift from 10% to 40% adoption, was 39 years for the
telephone, and 15 years for electricity, whereas both the television and the smartphone took about 2.5
years. With increasingly short cycles of innovation, and the growing complexity of technological systems,
some have noted that these systems are no longer comprehensible by humans (Arbesman 2016).
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Figure 1: 40 key and emerging technologies.
OECD (2016): Science, Technology and Innovation Outlook 2016. Paris: OECD Publishing.
The global economic shifts mentioned above, including the shifts in production and the expansion of
production capacities, especially in emerging economies, go hand in hand with an increase in research
and development (R&D) efforts in these key markets. Industry not only encounters a conducive
environment for R&D and prospective markets for innovation in these markets, but also ready access to
a large talent pool. The ongoing burst in innovation can be seen in the increasing number of patents,
which have doubled in number since 2002 and surpassed 3 million in 2016 (WIPO 2017). At the same
time, the development of the average gross domestic expenditure on R&D (GERD) per person shows a
clear upward trend and has increased globally from less than 1.5% of GDP in the late 1990s to 1.7% in
2015, according to UNESCO data. As this period witnessed substantial growth in the global economy,
per capita spending on R&D (in PPP) increased from an average of 95 US$ in 1996 to 263 US$ in
2015.2
Accordingly, a related development is the shift in innovation capacities, also with regards to chemistry
innovation. Using data by the World Intellectual Property Organisation (WIPO) as an indicator illustrates
these significant regional shifts (see Figure 2). Looking at the number of patents granted to a range of
chemistry-related fields, Asia surpassed North America and Europe in the early 2000s and has since
become a global innovation powerhouse, with more granted patents than all other regions combined.
Within Asia, China is leading the charge, with about twice as many patents as Japan, which in turn has
double the number of patents as the Republic of Korea.
2 Data taken from http://data.uis.unesco.org on 14 May 2018.
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Figure 2: Patent grants on chemicals-related innovations across regions.
Source: WIPO.3
Latin America and Africa show a more mixed picture with relatively little dynamic, apart from innovations
concentrated in individual countries. According to researchers from Africa, complex and lengthy
application processes pose a major obstacle for filing patents. Limited availability of public and private-
sector funds for R&D was cited as another constraining factor in many parts of Africa.
Figure 3: PCT patent publications on chemicals-related technologies.
Source: WIPO.4
3 Patent grants on: Organic fine chemistry; biotechnology; pharmaceuticals; macromolecular chemistry, polymers; food chemistry; basic materials chemistry; materials, metallurgy; surface technology, coating; micro-structural and nano-technology; chemical engineering. Settings used : Intellectual property right: Patent; Year range: 1987 – 2016; Reporting type: Total count by filing office; Indicator: 5 - Patent grants by technology.
4 Multi-national patent publications on: Organic fine chemistry; biotechnology; pharmaceuticals; macromolecular chemistry, polymers; food chemistry; basic materials chemistry; materials, metallurgy; surface technology, coating; micro-structural and nano-technology; chemical engineering. Settings used: Intellectual property right: Patent; Year range: 2000 – 2017; Report type: Yearly statistics; Indicator: 5a – PCT publications by technology. WIPO IP Statistics Data Center.
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When it comes to the utilization of these patents, data is harder to obtain. WIPO does provide data on
Patent Cooperation Treaty (PCT) publications by technology. As a PCT patent filing gives intellectual
property protection in many countries at once, it provides a better indication about the will to use this
knowledge. Asia is still the leading region for chemistry-related innovation based on PCT publications,
but its position is much closer to that of North America and Europe.
The increasing pace of innovation in the field of chemistry is also visible in the number of substances
registered with the Chemical Abstracts Service (CAS). The rate at which new chemicals are listed has
grown exponentially. It took the CAS 50 years to see the listing of 100 million substances, yet in just two
years since then, another 30 million chemicals were registered. Since 1965, on average one new
substance was registered every 2.5 minutes, and by 2016, this rate had increased to one new substance
every 1.4 seconds.
Figure 4: Number of chemical substances registered with the Chemical Abstracts Service (CAS).
Source. CAS.
Another noteworthy trend is that chemistry-related fields are among those technology areas with the
highest share of women inventors, at least based on data derived through the Patent Cooperation Treaty
(PCT) which allows for simultaneous patent protection in several countries. According to WIPO (2016:
14), biotechnology, pharmaceuticals, organic fine chemistry, food chemistry, and analysis of biological
materials are the five fields with the highest women’s participation rate, around or above 50%. Two
chemicals-related fields are at the top of the list of areas with the fastest growth in women participation
rates when it comes to patent applications, namely organic fine chemistry and food chemistry, both
increasing from around 30% in 1995 to more than 50% in 2015.
Digitalisation is one of the key technological developments and has a tremendous impact on many
industries, including the chemicals industry. Under the heading “Chemistry 4.0”, (Deloitte and VCI 2017)
the impact of digitalisation is considered to lead to drastic changes within the chemicals industry. Three
categories are seen as especially relevant: First, transparency and digital processes should allow
chemical manufacturers to monitor their internal processes and realize efficiency gains; second, data-
based operating models are expected to be used for decision-making, again, for enhancing efficiency;
and third, digital business models might “fundamentally alter existing processes, products, or business
models.” (Deloitte and VCI 2017:12). Important to note, an increase in digitalisation will correspondingly
translate into an increased demand in materials and energy.
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1.3. Impact on environment, Climate change, Resource use
Resource competition and scarcity are closely linked to climate change, population growth, increase of
income and health status (see 1.4). Importantly, this applies not only to mineral, fossil and bio resources,
but also to water, soil and air – the basis of all life – which are being heavily consumed and impacted by
the use of the resources mentioned as well as in industrial processing. Due to a growing population,
available remaining resources are in conflict. To reduce the risks and impacts of climate change and to
tackle increasing CO2 emissions, the 2015 Paris Agreement aims at “holding the increase in the global
average temperature to well below 2°C above pre-industrial levels”. To slow down global warming and
fulfil the Paris Agreement to meet the 2 Celsius degree scenario, industry among sectors such as energy
supply and transport, needs to take on a drastic transformation to support the needed reduction of
greenhouse gas emissions from 40% to 70% by 2050 (OECD 2016b). With a 50% contribution to global
CO2 emissions, China (29.5%), the United States (15.6%) and India (5.9%) are projected to have the
largest savings potential by 2030, and therefore could positively contribute to reducing global warming
by adopting low-carbon technologies (Roland Berger 2017).
Additional triggers negatively impacting climate change are population growth and urbanization,
particularly in emerging countries, contributing to an increase in energy demand and therefore further
human-induced causes of climate change. To fulfil the ambitious task of decreasing greenhouse gas
emissions, a substantial shift towards renewable energy and electro mobility has been promoted
globally, leading to new challenges. Technologies applied in batteries, wind turbines and solar panels
heavily rely on rare earth metals (dysprosium, neodymium, terbium, europium and yttrium). For example,
2 tons of neodymium is used to help drive strong light magnets to propel wind turbines. The renewable
and clean energy industry currently consumes around 20% of rare earth elements and other critical
materials (U.S. Department of Energy 2010). Short term forecasts predict that the mentioned metals are
at risk of supply chain disruption (U.S. DoE 2010). Additionally, the emerging middle-class in developing
countries has caught up to the developed world’s consumption patterns with major implications for rare
earth metals extraction. The shift from necessity to choice-based spending determines rising electrical
sales, resulting in a massive increase in e-waste. By China controlling 95% of rare earth metals supply
and its export reduction by around 40% due to high environmental challenges (Pool 2012; Hurst 2010),
the industry must foster research on tailing alternatives, substitutions, and recycling. Chemically, it is
less complicated to extract rare earth metals through mining than tiny amounts from a cell phone,
meaning recycling is a question of profitability (Jones 2013). As of today, e-waste recycling in Africa is
done by low-paid workers incinerating plastic to isolate materials. This in turn puts workers and the
environment at risk, while recycling in Japan is more and more automated (e.g. Honda announced in
2013 an in-house metal hybrid battery recycling programme, Honda Corp. 2013).
1.4. Demographic changes
Demographic change likely has the most pressing implications on the other presented megatrends in
this report. A rapidly growing population in Africa and Asia corresponding with a growth in the global
middle class will cause a change in consumption patterns, (e.g. increase in protein-based diets and
therefore, conflict in land use), as well as a shift from necessity-based spending to a choice-based (e.g.
increase in electronics sales). An ageing population in developed countries will likely correspond with a
shift from being economic power houses to social and health care-oriented societies. The chemicals
industry will need to provide innovations to improve living and working conditions for the labour force
(e.g. construction materials for an increasing urbanization, agrochemical solutions increasing yields and
combating post-harvest food loss), as well as technological innovations to be prepared to replace a
lacking work force in developed countries (e.g. robotics) and ensuring a comfortable living for the elderly
(e.g. pharmaceuticals, biomaterials).
In 2017 global population reached nearly 7.6 billion and is expected to increase to 8.6 billion in 2030
and 9.8 billion in 2050. By 2050, over a quarter of the global population will live on the African continent
and will remain especially high in 33 of the 47 least developed countries that are in Africa (UNDESA
2017; OECD 2016a). This development will likely lead to a growing middle-class and changing
consumption patterns, affecting resource scarcity, land use conflicts and increasing pressure on social
and health care systems. At the same time, a relatively young and well-educated work force will also
lead to an increase in the number of scientists, researchers and innovators battling the challenges of
the present and the future (OECD 2016a)
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Table 6: World Population Prospects.
Population in millions
Region 2017 2030 2050 2100
World 7.550 8.551 9.772 11.184
Africa 1.256 1.704 2.528 4.468
Asia 4.504 4.947 5.257 4.780
Europe 742 739 716 653
Latin America and the Caribbean 646 718 780 712
Northern America 361 395 435 499
Oceania 41 48 57 72
Source: United Nations Department of Economic and Social Affairs, Population Division (2017). World
Population Prospects: The 2017 Revision. New York: United Nations.
By 2050, the population on the African continent will also account for more than half of the global
population increase (OECD 2016a). Angola, Burundi, Niger, Somalia, United Republic of Tanzania and
Zambia are projected to be five times as large in 2100 as they are today. Should poverty, inequality,
hunger and malnutrition (in children under the age of 5) be reduced in parallel to increased and improved
education and health care systems, infant mortality rates would decrease and life expectancy would
increase, thus supporting further population growth. With fertility rates at 5.1 child births per woman or
higher in Africa, in contrast to 2.5 (2010 – 2015) in developed countries, Africa will likely have a young
working age population of 305 million in 2050, while children in the rest of the world will likely total 148
million (World Bank 2016; UNDESA 2017). A young working population across African countries would
support their research and development capabilities to adapt to future challenges and to increase the
livelihoods of their population.
In Europe on the contrary, the fertility rate is below the required replacement level, shifting economic
growth and resources towards social and health care spending. 25% of the overall population is already
over 60 years of age and is projected to reach 35% in 2050 and 36% in 2100 (UNDESA 2017). The total
population particularly in Eastern European countries such as Bulgaria, Croatia, Latvia, Lithuania,
Poland, the Republic of Moldova, Romania, Serbia and the Ukraine is projected to decline by 15%; this
also corresponds to a decrease in life expectancy to an average level of 72 years (2010-2015) (UNDESA
2017). Europe and North America account for half of the global middle-class with two thirds of the global
spending today (OECD 2016a). Innovations in these regions will likely focus on robotics to replace the
work force and to improve living conditions for the elderly (EY 2017a).
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1.5. Urbanisation
In 2008, for the first time in human history, more people lived in cities than in rural areas. In 1950, 30%
of all people lived in urban areas, and by 2050, it is projected that 66% of the global population will live
in cities. Combined with the ongoing demographic transitions and the expected population growth over
the coming decades, the total number of people living in urban settlements will grow by 2.5 billion people
by the mid-century, up from a total number of 3.9 billion in 2014 (UNDESA 2014a). This means that in
every week until 2050, there will be on average 1 million people moving to a city.
Figure 5: Global population living in urban and rural areas, 1950 – 2014 – 2050 (projected).
United Nations, Department of Economic and Social Affairs, Population Division (2014): World
Urbanization Prospects: The 2014 Revision – Highlights. ©2014 United Nations.
Reused with the permission of the United Nations.
North America (82% of the population live in cities), Latin America and the Caribbean (81%), and Europe
(74%) record relatively high rates of urbanization, which dynamics are hardly discernible in these
regions. On the other hand, Asia-Pacific (50%) and Africa (43%) are currently still much more rural
regions, and increased urbanization has a much higher impact there: About 90% of the 2.5 billion people
who will be moving into cities by 2050 are (and will be) living in Asia-Pacific and Africa (UNDESA 2018).
The number of large and mega-cities are projected to increase, as they will be home to more and more
people. While in 2014, 28 cities had more than 10 million inhabitants, by 2030, the number will have
increased to 41. A comparable increase is expected in cities of 5 to 10 million people, of which there
were 43 in 2014 and an expected 63 in 2030 (UNDESA 2014a).
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Figure 6: Growth of urban population by city size. Source: UNDESA 2014b.
United Nations, Department of Economic and Social Affairs, Population Division (2014): World
Urbanization Prospects: The 2014 Revision – Highlights. ©2014 United Nations.
Reprinted with the permission of the United Nations.
This rate and scale of urbanization will likely lead to a strong and ongoing need to develop accompanying
infrastructure, including housing and transportation. This would lead to significant urban sprawl, as more
than 60% of the land expected to become urban has yet to be developed (UNDESA 2014c). It has been
projected that much of this expansion will convert highly productive cropland and thus contribute further
to the pressure on agriculturally productive areas (Bren d’ Amour et al. 2016). This strong growth
demands massive resource use for construction purposes as well as for maintenance and use by
inhabitants (see also section 2.2 below). A widely cited statistic showed that China used more cement
in the three years 2011-2013 than the United States did throughout the entire 20th century (Swanson
2015).
By 2050, China will have to create housing for 292 million new urban inhabitants, which is only
surpassed by India, where 404 million people are expected to move to the cities (UNDESA 2014a: 56).
These staggering numbers represent a significant challenge for the involved municipalities and national
governments. Much of the migration into cities will be informal and many more people can be expected
to live in slums. While the percentage of people living in slums has decreased from 39.4% in 2000 to
29.7% in 2014, the absolute number of people increased from 791 million to 881 million (UNHABITAT
2016). Thus, the challenge is not only to build living space in itself, but to build sustainable, inclusive,
and affordable living space.
Urbanization also leads to changing needs for employment and mobility, food and a healthy
environment. New mobility models such as car-sharing, new technologies based on e-mobility, and low-
to zero-carbon transportation are thriving in cities. “Future cities built on driverless transit systems, smart
buildings and green spaces — all inhabited by connected and aware citizens — are already beginning
to emerge.” (EY 2017a: 41) While strong on innovation, the increasing demand for resource-intensive
food by growing urban populations poses particular challenges to agricultural areas (Satterthwaite et al.
2010). However, cities are not only hungry for food, but for all sorts of resources: Material consumption
of the world’s cities is expected to increase from 40 billion tonnes to 90 billion tonnes by 2050 (UN
Environment 2018a).
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1.6. Climate change and pollution
Climate change is majorly impacting all the presented megatrends. The interdependencies of climate
change and ecosystems are apparent: with global warming, the core of climate change is increasing.
Carbon dioxide emissions (CO2) are on the rise especially due to the economic growth in non-OECD
countries, putting the eco-system at risk. Additionally, Agricultural production now consumes nearly 70%
of groundwater, while industry consumes 20% and households 10%. Only 2.5% of global water
resources are fresh water, and only 0.3 % are easily accessible (Lauster et al. 2011). Presently, global
water demand has outpaced population growth and is projected to increase by 55% by 2050 (OECD
2016a). With a high-intensive agriculture, surface as well as groundwater quality is degrading and
therefore contributing to the spread of waterborne (e.g. bacterial spread, viruses, protozoa) and vector-
borne diseases (e.g. malaria, dengue fever) (USCRP 2018). Since waste water management
infrastructure has not been properly developed and implemented in most developing countries, the
chemical exposure to the environment and living beings remains high.
With the last 30 years being the warmest within the last 1400 years in the northern hemisphere, due to
a significant rise in greenhouse gas emissions mainly caused by an atmospheric carbon dioxide (CO2)
increase of around 40% since the 1880s (annual global temperature increase since then: 0.85 Celsius
degrees), most of these emissions have occurred since the 1970s when global energy consumption
began to rise substantially, in conjunction with an increase in methane (CH4), and nitrous dioxide (N2O)
(OECD 2016a; EEA 2014). The total greenhouse gas emissions in 2010 consisted of 76% of CO2, 65%
coming from fossil fuel combustion and industrial processes. 11% are caused by intensive agricultural
production processes and deforestation (EEA 2014).
Figure 7: Energy-related CO2 emissions per capita.
OECD (2016): Science, Technology and Innovation Outlook 2016. Paris: OECD Publishing.
Another impact of climate change is on natural ecosystems, including substantial losses of biodiversity
(33% loss from 2010 to 2030; Roland Berger 2017) and increased rates of extinction of coral reefs, the
Amazon forest and the boreal-tundra arctic. As of today, 40% of China’s arable land is suffering from
degradation (soil erosion, acidification) leading to a food crisis. Australia has already lost 40% of its
forests and Brazil 20% of its rainforest due to the transformation of supply chains towards 4 main
commodities: beef, soy, palm oil and pulp and paper. Argentina (40% loss of forests) and India (50%)
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are also facing a high share of land degradation through soil erosion, risking desertification and thus
agricultural productivity loss (Roland Berger 2017: 23). The Food and Agriculture Organization of the
United Nations (FAO) projects that food demand will increase by nearly 50% by 2050, corresponding
with population growth and an increase in per capita income, contributing to natural resource scarcity
and degradation (FAO 2017a). With a rise in population and consumption levels it is projected that it will
not be possible to provide enough land to simultaneously maintain agricultural production levels and to
maintain current natural areas, halt forest loss and completely switch over to renewable energy
production. Conflict of land use and global warming will influence the spread of transboundary plant and
pest diseases (Roland Berger 2017) in agriculture and therefore, lead to increase in agrochemical
development and innovations.
With regard to CO2 emissions Agriculture and fossil fuel combustion are the main drivers for climate
change, as well as freed-up methane from wetlands, leakages from natural gas systems and livestock
production (Roland Berger 2017). A further impact of the triggers mentioned above is air pollution due
to intensifying energy use. Fossil fuel burning from coal and petroleum and mining processes release
sulphur dioxide into the atmosphere, contributing heavily to air pollution and acid rain. The transportation
sector and producing industries are responsible for releasing carbon monoxide, hydrocarbons and
organic compounds. Among the drawbacks of urban life are the negative health effects of air pollution.
The World Health Organization (WHO) estimated that 98% of cities in low- and middle-income countries
and with more than 100,000 inhabitants did exceed air quality guidelines for safe levels of particulate
matter. Ambient air pollution leads to between 3.0 and 4.2 million deaths per year (Landrigan et al.
2018). Cities will thus continue to be the main centres where many of the key challenges of sustainable
development are felt and need to be addressed. Generally, most air pollutants are expected to increase,
particularly nitrogen oxides (transport and power generation) and ammonia (agriculture) (OECD 2016b).
Air pollution causes 6.4 million deaths a year globally (EDF 2018). While in OECD countries it is
projected that air pollution will decrease due to a shift towards low-carbon technologies and innovative
(chemical) materials for various industry sectors, expectations are not the same for the non-OECD ones.
Air pollution is expected to increase massively, predominantly in urban areas, due to the expansion of
housing, automobiles and their corresponding energy production.
The potential for the chemical industry lies in taking on the model of the circular economy. Also further efforts are needed towards achieving more energy efficient processes. In addition to the usual efforts of chemical industry other matters have to be explored, e.g. the potentials of the circular economy, the use of waste and side streams of other industries for the chemical industry etc.
Sustainably grown non-food biomass and biotechnology positively contributes to a replacement of the
oil and petrochemical industry through the development of bio-based batteries for e-mobility, as well as
research on artificial photosynthesis processes and micro-organisms for biofuel production. Another
innovation opportunity is additive manufacturing, using less material saving energy through production
processes and intelligent design (OECD 2016a). Unfortunately, climate change will not be stopped —
society must adapt to the upcoming challenges, including agricultural production shifts, rising sea levels,
changing weather patterns etc., by implementing measures to increase resilience.
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2. Sectoral Outlooks: Chemicals Risks and Innovation
Opportunities in Key Industry Sectors
In the following sections, innovation opportunities are mentioned, that potentially contribute to more sustainable solutions. However, any disruptive innovative approach has to be checked carefully for impacts to avoid a transfer of challenges and risks into another sector or into the future. Sustainable chemistry can serve as a guiding principle to avoid such follow up problems (Kümmerer 2017). How do we know that an innovation is sustainable or at least more sustainable than another one or the existing technology and products? Cement production will still need large amounts of energy and result in large amounts of carbon dioxide emission along its supply chain, even after significantly improving the sector. The Power to X approach is interesting. However, despite all on-going research and its emerging practical implementation it is not yet clear whether it will be (more) sustainable or greener even when renewable energy is used for electrochemical synthesis of organic molecules from CO2. Digitalization (chemical industry 4.0) may hold a potential for more sustainability in industry. However, the increased application of software systems translates to a higher demand for hardware and energy. These few examples demonstrate the complexity of assessing sustainability. Many criteria, specific situations and circumstances of application have to be taken into account. This warrants a systems thinking that we are just at the beginning of understanding. The following considerations and case examples were chosen to exemplify both the opportunities and the pitfalls of innovations in different sectors.
2.1. The chemicals industry and the relevance of megatrends for chemicals
management and innovation
In 2016 the global chemicals industry had a total revenue of EUR 3,360 billion (about US$ 4 trillion), but
is expected to more than double by 2035, fueled largely by China’s substantial supply and demand in
chemicals (Cefic 2018; Roland Berger 2015). Due to China’s ambitious transformation process—driven
by urbanization, a rising middle-class, changing consumption patterns and dedicated support to
implement the Paris Agreement on lowering CO2 emissions—China has shifted from a net importer to
a net exporter of chemicals in terms of sales. Its growing manufacturing base focused on production of
high-value chemicals and plastics will secure China a 62% share of the global market in 2035 (CEFIC
2017; Roland Berger 2015). While China is on the rise, Europe and the United States are confronted
with a declining market share of chemicals sales. A 56% increase in the number of EU regulations for
the chemicals market since 2008 is one of the main drivers for rising costs with regard to research and
development, aside from high energy and feedstock costs in the EU (Roland Berger 2015). The United
States, on the other hand, is benefiting from its access to shale gas, which contributes to a net addition
of 9% of global CO2 emission together with the Middle-East (Deloitte 2017).
Linking the global chemicals industry to the megatrends outlined above, the chemical production is
expected to significantly increase in the future, and will also be discussed in more details in the following
paragraphs on industry sectors. Due to an increase in urbanization, especially in emerging countries,
the demand of construction materials and innovations in the automotive sector will lead to a rise in the
speciality chemicals market, also closely linked to an ongoing development of technology. Growing
demand for construction materials, packaging, transportation, textile, plastics and health care, coupled
with low oil prices will lead to an increase in petrochemicals, not only causing India and China to
establish additional petrochemical production capacities, but also leading to a shift in production control
by OPEC. The fertilizer and agrochemicals sector will be heavily influenced by climate change,
population growth and urbanization. An increasing end-user demand will not only affect agricultural
production, but also international trade patterns and environmental laws and regulation. New
technologies in agricultural biotechnology, genomics and organic farming will shape the future of the
agrochemicals market (EY 2017a). At the same time, identifying sustainable solutions for customers,
and enhancing their own sustainability performance, are key challenges for the chemical industry (EY
2017b).
The overall growth of the chemicals market will be driven by China and the Middle-East (around 12%,
Deloitte 2015), while Europe’s growth will decline to 5%, leading to a global market share in 2035 of
13% (Roland Berger 2015). The mergers and acquisitions in the chemical industry with Germany, China
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and U.S. leading the way (Bayer-Monsanto, ChemChina – Syngenta, Dow – DuPont) are valued at a
global worth of $231.1 billion in shuffling portfolios with regard to intermediates and specialty chemicals,
strongly focused on agrochemicals. In response to the growth of the convergence of seeds and
pesticides, companies are trying to close the gap between research and development in plant genetics
and crop protection (Deloitte 2017). In the following paragraphs the industry sectors linked to the
chemicals industry will be discussed in more detail.
2.2. Agriculture and food
A growing world population will increasingly affect the means of conducting agriculture in future. The
FAO estimates that overall food production needs to increase by about 50% by 2050 (FAO 2017b).
Meeting this need through a further increase in farmland acreage by e.g. deforestation is not desirable
due to downstream problems such as the destruction of natural habitats and of CO2 sinks. An alternative
approach discussed is the intensification of agricultural practices (IFA 2016). However, instead of just
increasing business-as-usual practices, environmental impacts should be limited in future.
2.2.1. Status and forecast of the sector
The global Agrochemicals market had a value of US$ 215.18 billion in 2016 and is projected to grow up
to US$ 250.5 billion by 2020. Agrochemicals describe the products used in the field such as crop
protection like insecticides, fungicides, herbicides and nematicides, as well as fertilizers (biological and
synthetic) and chemical growth products (Market Insights 2018). Due to an increasing population and
urbanization as discussed in the megatrends above, additional pressure is released on the agricultural
sector facing diminishing farmlands, soil erosion and contamination and water scarcity. Nevertheless,
the use of agrochemicals leads to yield increase and the adoption of dual cultivation, due to fertilizer
usage maintaining soil fertility. These factors are pushing the increasing development and growth of the
agrochemicals market of China and Japan, being the largest producers and North America and Asia-
Pacific as largest consumers. With an upcoming rapid population increase linked to economic growth in
China and India, forecasts predict that these countries will ensure the positioning of Asia Pacific “as
fastest growing market for agrochemicals” (The agrochemical market in India is estimated to grow at
7.5% annually, to reach US$ 6.3 billion by 2020, Market Insights 2018).
2.2.2. Potential concerns from a human health and environment perspective
In Sub-Sahara Africa, where farmers use way below the global average of nutrients (10-15 kg per
hectare), the nitrogen use efficiency (NUE) lies way above 100%, going hand in hand with low
agricultural productivity and soil depletion. India, on the other hand, was observed to make excessive
fertilizer use, also propelled by a government subsidy, which has led to less and less increased yields,
compared to the nitrogen input. The International Fertilizer Association (IFA 2016) attributes this trend
to the governments increasing focus on resource efficiency. In developed countries such as the US,
Western Europe, or Japan, the past thirty years have shown a continuous improvement of NUE. A trend
attributed to the uptake of fertilizer best management practices in these regions, according to the IFA
(2016). These observations match the overall trend of NUE over time: at first, with no or very little
nitrogen added, NUE lies over 100% but leads to extensive soil nitrogen depletion. The more nitrogen
is added, at first, yield output increases, reaching a tipping point, after which the yield output per added
unit of nitrogen input would decrease. However, it has been observed that due to the implementation of
more sustainable intensification and, in particular, fertilizer best management practices, the NUE
improves, though it will not be able to reach 100% due to natural losses of nitrogen (IFA 2016). One
exception to this development is Brazil. The country has, due to access to improved technology and a
large proportion of soybeans in its crop mix, managed to circumvent a decline of NUE.
The above described megatrends of population growth and changing consumption patterns are both
expected to lead to an increase in the global demand for fertilizers. However, the mix of fertilizers is
estimated to become more diverse (increase of phosphate and potassium fertilizers, comparably slower
increase of nitrogen fertilizers), due to the need for more balanced application of fertilizers to increase
the yield output in the long-term (IFA 2016). Demands of nitrogen fertilizers are expected to shift away
from the Asian region towards Africa and Latin America, while supply of nitrogen fertilizers is expected
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to increase in countries with access to natural gas or coal reserves, due to increased investments in
capacities of ammonia and urea. Exports will continue to come predominantly from Eastern Europe,
Central Asian and West Asia, while imports are expected to continuously go towards South Asia (India
in particular) (ibid.).
Despite various advantages of agrochemical use, the negative impacts are yet significant. The decrease
of soil fertility, intoxication of helpful microorganisms and microbes, as well as increasing pH levels are
only a few to name. Also, important to highlight is ground water pollution and the disturbance of aquatic
life. The excessive use of nitrate-based fertilizers leads to ground water contamination risking for
example immobilization of hemoglobin and a reduction of oxygen within the human body. Furthermore,
the pesticide usage such as DDT, dieldrin and aldrin are not only causing severe impacts on the
environment, but also on all living beings. With a high-intensive agriculture, surface as well as
groundwater quality is degrading and therefore contributing to the spread of waterborne (e.g. bacterial
spread, viruses, protozoa) and vector-borne diseases (e.g. malaria, dengue fever). Since waste water
management infrastructure has not been properly developed and implemented in most developing
countries, the chemical exposure to the environment and living beings remains high. Therefore, the
chemical industry increased its efforts to substitute toxic chemicals with non-toxic alternatives also taking
on the organic food market by providing effective products. However, measures at the source including
the products themselves are first choice (Kümmerer et al. 2018).
2.2.3. Opportunities for sustainable chemistry innovation
Biological alternatives to synthetic or chemical fertilizers, pesticides, or stimulants are meeting a growing
demand for food that is sustainably grown and respond to stricter governmental regulations that aim to
protect humans and the environment. At the same time, the industry becomes more and more aware of
the benefits of such soil treatment that sustainably increases yields. However, this is not to say that the
market grows at a speedy pace: The North American market for agricultural biologicals, which is leading
before Europe and Asia Pacific is expected to grow from 2.08 billion US$ in 2016 towards 6.82 billion
US$ in 2025. Quite similar trends are expected for the European market (from 1.62 billion US$ in 2016
towards 5.36 billion US$ in 2015), where in 2014, around 10.3 million hectares of farmland was cultivated
organically, predominantly in Spain, Italy, and France. With an estimated growth from 1.25 billion US$
in 2016 towards 5.59 billion US$ by 2025, the market for agricultural biologicals in Asia Pacific is
expected to surpass the European market. Reasons are the not so much increased governmental
regulations, but the expected increase of population which leads farmers to be reliant on higher yields
and enhanced nutrient and plant growth that is promised by biological techniques. The majority of the
3.6 million hectares of organically cultivated farmland in the region in 2014 were found in China, followed
by India.
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2.3. Construction
2.3.1. Status and forecast of the sector
The global construction industry is expected to grow to a total market value of 10.5 trillion US$ by 2023,
according to Research and Markets (2017), and to 15.5 trillion US$ by 2030, according to Global
Construction Perspectives and Oxford Economics (2015). In the latter study it is estimated that the USA,
China and India alone will account for 57% of global construction growth by 2030. Together with
Indonesia, UK, Mexico, Canada and Nigeria, just eight countries will account for 70% of global
construction growth. Among these, India is the fastest growing construction market and expected to
become the third largest market by 2030 but hampered by poor infrastructure and difficulties with running
businesses. CO2 emissions of the global construction industry are estimated at 5.7 billion tons in 2009
(Huang et al. 2018).
Ongoing urbanization is one of the main drivers of construction growth. Whereas in 2014 about 4 billion
people lived in cities, that number is expected to increase to more than 5 billion by 2030 and to almost
6.5 billion by 2050 (UNDESA 2014a). Building infrastructure for 2.5 billion people in about 25 years is a
tremendous and resource-intensive challenge. Apart from urbanization, global and localized impacts of
climate change, (latter especially in combination with increasing urban density and the related heat
emissions), lead to a need for climate adapting housing and commercial facilities (e.g. heat-/cold-
proofing, adaptation to more intensive rain/humidity, and extreme weather protection such as against
excessive winds or flooding).
At the same time, growing disposable income by the growing urban middle class leads to increasing
investments in living comfort and consumption. Emerging sustainable and healthy consumption patterns
are mirrored by growing concerns for healthy living environments (e.g. avoidance of exposure to (semi)
volatile organic compounds (SVOCs/VOCs) from wall paints, flooring, or other materials).
Case study: Pyrethroids
Similar to the naturally occurring pyrethrins, found in Chrysanthemum cinerariaefolium and
Chrysanthemum coccineum, their synthetic relative, pyrethroids, are compounds used in pest control.
By paralyzing the nervous system of the insects whose organs they have infiltrated, they became a
popular ingredient to insecticides. The global market value of pyrethroids is expected to grow from
US$ 3.82 billion in 2016 towards US$ 5.71 billion in 2015.Though they find their uses, not only in
agriculture, but also in homes or schools, pyrethroid pesticides are known to negatively affect the
aquatic ecosystem. The largest global market share of pyrethroid product types is owned by bifenthrin
with 35% in 2016. Though the market prognosis estimates a slight drop, bifenthrin is expected to retain
its market dominance. Permethrin, which is used as an insecticide and also a medication for treatment
of scabies and lice, was indicated to be the most effective and safest medicine by WHO’s List of
Essential Medicines, and is expected to increase its market share as a medicine in future.
Pyrenthroids are most commonly and increasingly used in Asia Pacific (the market growing particularly
fast in China and India), predominantly as pest control in agriculture and repelling of insects. Such
insect repelling products are on the rise, since cases of vector borne diseases such as dengue or
chikungunya have recently increased in the region and regulating bodies have taken initiatives to halt
them. Europe, the second largest market for pyrethroids, is expected to grow, due to the ban on
nicotinoid pesticides (clothianidin, imidacloprid, thiamethoxam), which are known to harm bee
populations, and subsequently need substitutes.
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The global market for construction chemicals is expected to grow by 9% per year and increase to more
than 50 billion US$ by 2025 (Global Market Insights 2017). Construction chemicals are commonly sorted
into five categories (ibid):
• Concrete admixtures
• Protective coatings
• Asphalt modifiers
• Adhesives
• Sealants
Regionally, the growth in the construction chemicals market may be much larger. Especially in the fast
growing and massively urbanizing Asian and African markets, higher growth rates have been observed.
For example, India expects a steadily increasing growth rate (CAGR) of 17.2% from 2016 – 2020, to
reach a market size of 1.89 billion US$ (Bahadur 2017).
Global cement use is expected to increase from currently 3.5 billion tons per year to more than 5.5 billion
tons in 2050 (Global Construction Perspectives and Oxford Economics 2015). Other researchers agreed
that there will be a rapid increase of cement production in the coming decades, but that it would slow
down and reach 4.2 billion tons in 2050, a figure which might be considerably lower if a high carbon tax
would be imposed on CO2 emissions for the sector (Ruijven et al. 2016).
2.3.2. Potential concerns from a human health and environment perspective
Construction chemicals can pose serious harm to workers on construction sites, and in the case of
offices or housing also to office workers and inhabitants. Especially in developing countries, asbestos
remains a very serious hazard. The WHO estimates that 125 million people in the world are exposed to
asbestos in the workplace, and the diseases associated with occupational exposure led to the deaths
of 107,000 people (WHO 2014). Another source of hazardous chemical pollution are plasticizers, which
are commonly used in products like polyvinyl chloride (PVC). PVC materials are a major source of indoor
chemical residues of substances like DEHP, which have been linked with asthma (Jaakkola; Knight
2008; but see Kanchongkittiphon et al. 2015). Especially in the case of asbestos, exposure can take
many years before the most serious health effects become visible.
Everyday exposure is nevertheless a common source of problems for workers. In a study based on a
questionnaire filled in by more than 30,000 Dutch construction workers, it was reported that on average
6.4% of them complained about gases and vapours, with much higher figures for asphalt workers (53%)
and road markers (45.9%). An average of 4.6% complained about smoke, while among road markers
(31.4%) and pile drivers (32.7%) were considerable higher. An average of 8.0% complained about
chemicals, and here the highest share of workers who complained was among concrete repair men
(61.8%), epoxy/polyurethane floor layers (45.7%, terrazzo workers (36.4%), painters (34.3%) and
sealant/polyurethane foam appliers (29.5%) (Tienen; Spee 2008).
A number of chemicals have been recommended by various stakeholders to be avoided or replaced in
the construction industry. The US Green Building Council published a list containing hazardous
chemicals such as asbestos, cadmium, mercury, chromium(VI), polyvinyl chloride, phthalates, bisphenol
A, perfluorinated compounds and all carcinogens listed in California Proposition 65 for projects on US
territory, and for projects outside the US carcinogens listed on the REACH substances of very high
concern (SVHC) Candidate List. Other stakeholders have likewise published lists of substances to avoid
in construction, for example the “red list” by the International Living Future Institute or the Cradle to
Cradle Banned Chemicals List.5 Replacing these substances is a key challenge for sustainable
chemistry innovation.
5 US Green Building Council : LEED BD+C: New Construction | v3 - LEED 2009: Avoidance of chemicals of concern. Online at https://www.usgbc.org/credits/new-construction-core-and-shell-schools-new-construction-retail-new-construction-healthcar-8, accessed 9 May 2018; International Living Future Institute: The Red List. Online at https://living-future.org/declare/declare-about/red-list/, accessed 9 May 2018; Cradle to Cradle Certified™ Banned List of Chemicals. https://www.c2ccertified.org/resources/detail/cradle-to-cradle-certified-banned-list-of-chemicals, accessed 30 May 2018.
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2.3.3. Opportunities for sustainable chemistry innovation
Enhancing sustainability is one of the key challenges for the global construction sector (World Economic
Forum 2017). The emerging circular economy thinking in the construction sector requires the
incorporation of recyclability of construction materials, with the reduction of negative externalities as one
central aim (Lemmens; Luebkeman 2016). This pertains specifically to chemicals, as these can pose a
serious barrier to circularity. As one review noted, while there is general awareness of the circular
economy concept in the sector, its application is “in its infancy.” (Adams et al. 2017) A range of policy
instruments exists which could be used to accelerate the transition towards a circular economy
specifically in the construction sector (Høibye; Sand 2016).
While a building may serve its purpose for residential housing, commercial or industrial activities or
leisure/entertainment, it may also be considered as a material base. To this regard a linkage between
digitization and construction will open new opportunities but also new requirements to construction
material suppliers (cf. Roland Berger 2016). As of now, construction is among the least digitized sectors,
showcasing both the need and opportunities to companies to become active there (Agarwal et al. 2016).
Plastic is a widely used construction material and about 21% of the 47 Mt of plastic used in Europe go
into the construction sector (Plastics Europe 2012). However, plastic pollution is already a pressing
global environmental problem (Ellen Mac Arthur Foundation 2017b). While some uses of plastic in
construction can come with considerable environmental benefits, e.g. frames for insulation windows,
and may be well recyclable, others pose challenges at the end of their life-cycle. Sustainable chemistry
innovation can reduce the need for fossil fuels and thus contribute to mitigate the climate change. But it
must not necessarily lead to plastic which is more benign at the end of the life-cycle.
2.4. Energy
2.4.1. Status and forecast of the sector
While growing concern and efforts for increasing energy efficiency for residential, commercial, industrial
purposes and transport continue making inroads, population growth and continuing industrialization are
expected to result in a growing energy demand in the coming decades by nearly one third until 2040
(IEA 2016). The Electronic Industries Alliance (EIA) organization estimates that the total world energy
consumption is expected to rise from 575 quadrillion British thermal units (Btu) in 2015 to 736 quadrillion
Btu in 2040.
According to an assessment from the IEA (2017), an increasing number of energy efficiency regulations
have contributed to a clear slowdown in energy demand growth. In the IEA New Policies Scenario,
demand growth will further slow (from an average of 8% per year from 2000 to 2012 to less than 2% per
year since 2012) to an average of 1% per year until 2040. Without new efficiency measures, end-use
consumption in 2040 would be 40% higher. In line with the view of IEA, the global energy outlook of
ExxonMobil (ExxonMobil 2017) reiterates that electricity generation will be the largest and fastest
growing demand sector, reflecting strong growth in global electricity demand. The oil demand will grow
to support commercial transportation and chemical needs.
In the emerging energy scenario, the 2040 per-capita energy consumption in China will exceed that of
the European Union (EU). According to the IEA, global trends will be determined by China’s choices,
which could spark a faster clean energy transition. The influence of Chinese vehicle manufacturers in
launching electric vehicles (EVs) is a commonly cited example. The New Policies Scenario assumes
that one-third of the world’s new wind power and solar PV will be installed in China. China will also
account for more than 40% of global investment (in EVs).
By 2040, the non-OECD share of global energy demand is expected to reach about 70%, as efficiency
gains and modest economic growth help keep OECD energy demand relatively flat. China and India
together account for about 45% of world energy demand growth to 2040. (ExxonMobil 2017)
The overall energy demand in the transport sector is also projected to increase due to an initial increase
in personal mobility demands, which will peak sometime between 2020 and 2025. However, the growth
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in economic activity and disposable personal income is expected to drive increasing trade of goods and
services, leading to higher energy demand in the commercial transportation sectors. The largest growth
by volume is expected in heavy duty transportation, but marine and aviation are projected to grow the
largest by percentage. The development of regional energy demands in the transport sector mirrors the
economic growth (GDP) outlook of different regions, with the majority of growth in commercial
transportation is likely to occur in the non-OECD countries.
Figure 8: Change in world primary energy demand by fuel.
© OECD/IEA 2017 World Energy Outlook, IEA Publishing. Licence: www.iea.org/t&c
Similar regional differences can be noted with regard to the development of residential and commercial
energy demands. Overall population growth, growth in households, rising prosperity and expanding
commercial activity are expected to trigger higher demand for lighting, heat and power in homes (e.g.
increased use of home appliances and amenities such air-conditioning, cooling, heating) and offices,
resulting in a rise of about 25% by 2040 (non-OECD countries 40%). The African region and China will
each account for about 30% of the increase in demand in this segment (ExxonMobil 2017).
As the largest group of energy consumers, industrial activities account for around 50% of global energy
demand, which is projected to grow by about 25% during the period 2015 – 2040. The heavy industry
sector will continue to take the largest share. Improvements in energy efficiency in industrial processes
are expected to moderate the overall industrial energy demand growth. With heavy industry shifting to
other emerging markets such as to India, Africa and Southeast Asia, the corresponding industrial energy
demand will also change.
Within this segment, the chemical sector sees the highest growth in energy demand with around 45%
during period from 2015 to 2040. The demand for chemical products is expected to outpace GDP in
many emerging markets, such as in Asia. Economic and population growth, rising prosperity and
disposable income as well as urbanization fuel the demand for fertilizer (increased food production),
plastics (e.g. packaging) and other chemical products.
2034
607
19
7
1407 1268
840
1277
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Figure 9: Number and share of people without access to electricity by country, 2012.
© OECD/IEA 2014 Africa Energy Outlook, IEA Publishing. Licence: www.iea.org/t&c
With the relocation of chemical production closer to these emerging markets, the chemical industry will
add to the regional energy requirements. In addition to local demands, access to low cost feedstocks is
a crucial competitive factor. In the Middle East, feedstock availability drives the petrochemical industry
evolution. With feedstock accounting for about two-thirds of chemicals energy, the energy demand is
expected to more than double.
2.4.2. Potential concerns from a human health and environment perspective
According to the British Petrol Statistical Review of World Energy, June 2017, oil, gas and coal account
for 85% of the world’s primary energy consumption, thus contributing to about 2/3 of greenhouse gas
emissions. As per the IEA World Energy Outlook, a transformation in electricity and heat generation
would be of need to meet the targets in the international climate change agreement. A possible
decarbonisation of the energy sector would require a combination of starting points, considering (a)
increasing energy efficiency, (b) expanding renewable energy, (c) reducing resource consumption and
(d) reducing pollutant emissions during the use of fossil fuel sources (BMU 2018). By 2040, around 37%
of the global gross power supply might be met through renewable energy sources (IEA 2016), while the
remainder will be supplied by energy from fossil sources. However, electricity is the rising force among
worldwide end-uses of energy, making up 40% of the rise in final consumption to 2040 – the same share
of growth that oil took for the last twenty-five years (IEA 2016).
The Agenda 2030, SDG 7, strives towards securing access to affordable, reliable, sustainable and
modern energy for all. For example, in early 2018 India announced its plan to achieve 100%
electrification of households. Corresponding strategies will need to address resource efficiency and
climate friendliness of energy generation, storage, distribution and use. Urbanization and geographically
concentrated industrialization require not only a sustained supply of electricity (whether locally
generated or effectively transmitted), but also result in growing energy demand for the transport of
people and goods. The continued economic interlinkage of supply chains is also reflected by the growing
energy demand for intra and interregional movement of goods.
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2.4.3. Opportunities for sustainable chemistry innovation
As far as energy efficiency, efforts may focus on (a) energy efficient production processes, (b) energy
efficiency of buildings, (c) energy efficiency of tools and gadgets as well as (d) supportive technologies
(energy monitoring, metering & management, pumping systems, heat exchangers, etc.). The global
market for energy efficiency technology is expected to grow from US$ 995 billion (2017) to US$ 1781
billion by 2025. In a similar fashion the global market for environmentally friendly technology in
generation, storage and distribution of energy will nearly double during the same period (2018: US$ 796
billion; 2025: US$ 1390 billion) (BMU 2018: 48). In the latter segment, renewable energy technologies
will account for around 53%, followed by technologies for environmentally friendly use of fossil fuels
(25%), efficient distribution technology and storage technologies. Hereby, the segment for energy
storage technologies will increase by nearly 16% from 2017 to 2025 (BMU 2018).
The renewable energy mix is still dominated by hydropower as the single largest segment (31%), but
solar (19%) and wind (22%) are expected to account for nearly 50% by 2025.
The overall increase of electricity generation from renewables is mirrored by related growth in the job
market. In 2017, the number of jobs in the renewable energy sector surpasses 10 million for the first
time (IRENA 2018).
With the increase in renewable energy sources, the question of effective energy storage to make energy
available when and where actually required, is increasingly coming to the forefront. For example, issues
such storage efficiency and capacity are key topics in furthering e-mobility.
Case study - Power to X
A flexible utilisation of energy from volatile renewable sources may rely on converting power into
another form such as power to gas (hydrogen, methane), power to liquid (e.g. synthetic fuel) as well
as power to chemicals. For example, the SOLETAIR initiative (by INERATEC, an off-shoot of the
Karlsruher Institut für Technologie, Germany and the Lappeenranta University of Technology, Finland)
explores the conversion of carbon dioxide into a synthetic fuel with the help of solar energy. In a first
step, the pilot unit, which fits into a regular shipping container, splits hydrogen and oxygen using
electrolysis. During the second steps, carbon dioxide is converted into carbon monoxide, followed by
a Fischer–Tropsch synthesis to liquid hydrocarbons. While Power-to-X technologies seem to be
promising in the valorisation of a new, not primary fossile carbon source (CO2), the environmental
impacts of these Power-to-X pathways need to be assessed critically. Current investigations are often
focussed on the carbon footprint of CO2 conversion processes, thereby underestimating the high
resource demand (e.g. rare earth elements, metals, difficult to recycle composite materials) of the
entailed process chains starting from renewable electricity, CO2 and water supply, electrolysis and
subsequent conversion processes.
According to the German Association of Chemical Industry (VCI) chemicals will play a central role in
incorporating resource efficiency and climate friendliness of energy generation, storage, distribution and
use. In its assessment of the future of energy storage (VCI 2014), VCI concludes that to balance the
increasing fluctuations in the supply of renewable energy (such as wind, solar), energy storage apart
from distribution networks is indispensable. Chemical energy storage is comparatively better suited to
facilitate excess electricity over long periods of time as large quantities (e.g. electrolytically generated
hydrogen or synthetic methane). Whether for commercial or private use, energy storage systems meet
life-style and mobility demands.
Such systems will play a crucial role in distributed generation, under which power generation takes place
on-site at the point of consumption without relying on long distribution networks. The solar PV segment
is expected to hold the largest and fastest growing segment in the market (Coherent Market Insights
2016). Due to the decreasing cost of the solar photovoltaic cells, often combined with subsidy schemes,
an increase in the number of installations of the solar photovoltaic (SPV) has been observed globally.
The US Solar Energy Industries Association (SEIA) reported the U.S. installed SPV capacity to grow
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from 2,031 megawatts (MW) in 2017 to 49.3 gigawatts (GW) of total installed capacity by 2025. Apart
from home use and isolated solutions, the distribution of large scale solar PV hybrid plants in several
developing countries such as Kenya, Bangladesh, and Indonesia are expected to fuel the growth of
distributed generation market in this segment. By terms of geographical regions, apart from Africa, Asia
Pacific is estimated to be the major revenue contributor due to the lack of a reliable grid infrastructure
especially the Southeast Asian countries, where the population is spread across several islands, will
drive the demand for off-grid power systems in the near future (Coherent Market Insights 2016; 2017).
With many first-generation solar panels nearing their end of life, the challenge of adequate disposal
comes to the forefront. For example, in November 2016, Japan’s Environment Ministry warned that the
amount of solar panel waste Japan produces every year would rise from 10,000 to 800,000 tons by
2040, and the nation had no plan for safely disposing of it. In Europe, photovoltaic waste management
falls under the European Waste Electrical and Electronic Equipment Directive (WEEE). Incorporating
Extended Producer Responsibility (EPR) concept, the WEEE requires the original producers of these
goods to ensure their take-back and recycling within the countries of the EU. End consumers must not
face any additional cost at the moment of the disposal. The revised version of 2012 introduced a
provision on the disposal of photovoltaic (PV) modules for the first time. A similar spectre is being raised
about the future management of energy storage provisions.
Case study – Innovative environment friendly energy storage systems
With renewable energy supply on the rise, the integration with flexible and scalable energy-storage
solutions is necessary to mitigate output fluctuations. In view of the growing demand availability of
crucial materials for high-density and high-performance systems is becoming limited. Setting out to
develop an affordable, safe, and scalable battery system, the Center for Energy and Environmental
Chemistry (CEEC) Jena, Germany, has developed a redox battery using organic polymers as the
charge-storage material in combination with inexpensive dialysis membranes, which separate the
anode and the cathode by the retention of the non-metallic, active (macro-molecular) species, and an
aqueous sodium chloride solution as the electrolyte. According to the CEEC research team, this water-
and polymer-based redox flow battery has an energy density of 10 watt hours per litre, current
densities of up to 100 milliamperes per square centimetre, and stable long-term cycling capability. The
polymer-based redox flow battery uses an environmentally benign sodium chloride solution and
cheap, commercially available filter membranes instead of highly corrosive acid electrolytes and
expensive membrane materials. Given its simple processing methods the versatility of polymers in
batteries opens the potential for a wide range of application, such as „printed foil batteries. Such
printed batteries could be applied to smart packaging or apparels (Janoschka et al. 2015).
2.5. Transportation / automotive
2.5.1. Status and forecast of the sector
Urbanization and population growth increase the need for intra-urban transport as well as movement of
goods from supply to consumption areas. Furthermore, a growing consumer middle class that also
implies changing consumption patterns particularly in emerging economies, will lead to continuous
(though slightly lower, from 3,6% from 2001-2016 to about 2% by 2030) growth in global car sales
(McKinsey 2016). As such, the World Bank (2017) estimates that by 2050, there will be twice as many
vehicles on the roads compared to today’s 1 bn.
At the same time, personal mobility patterns, particularly in the urban areas are changing, which will
lead to a lower growth rate in personally owned vehicle as well as acceptance of alternative modes of
transports (public, bicycles), particularly in Europe and North America (Pucher; Buehler 2017). As one
reason for increased shared mobility, McKinsey (2016) names a greater diversification of vehicles that
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is targeted at different specific uses, and estimates that by 2050every third new car could be used for
shared mobility.
Along these lines, but at first sight quite ironically, personal car inventories are expected to decrease by
2030 in Europe and the US (by 29% and 22% respectively), while sales of new cars are expected to
increase (by 34% and 20%, respectively). In China, both the inventory of personal cars and the sales of
new cars are expected to increase by 53% and 30% respectively (PwC 2018). Unsurprisingly in this
respect, PwC (2018) estimates that such developments will take place at different paces in different
regions. As such they estimate that by 2030, the amount travelled by individuals will increase by about
23% in Europe and 24% in the US, but by 183% in China.
PwC identify four megatrends for the transport sector, namely, increased connectivity of vehicles, that
will allow for traffic to be organized more easily in the future, autonomous driving, that will come along
with further technical advances, shared mobility, and a substantial increase in electric cars (it is
estimated that about 55% of newly sold cars in 2030 will be electric cars).
2.5.2. Potential concerns from a human health and environment perspective
Rodrigue (2017) states that transport negatively impacts the environment by contributing to climate
change, impairing the quality of air, water, and soil, as a cause of noise, biodiversity loss, and land-loss.
Similarly, as early as 2000, WHO (2000) indicated that transport noise, transport accidents and injuries,
as well as air pollution were the main impairments of transport to human health. Not only due to the
combustion engines in the automotive sector, transport heavily contributes to greenhouse gas
emissions, and thus, to climate change. Maritime transport, moving 80% of the globally traded goods
from A to B, is a heavily polluting business (Vandyke; Englert 2017). While the shipping industry
accounts for a share of 2-3% of global greenhouse gas emissions, the sector continues to grow, which
has led the International Maritime Organization to project growth scenarios of increased emissions by
50% - 250% (IMO 2015). At the same time, the use of highly polluting residual fuel oil, high in sulfur,
poses a particular threat to human health and the environment.
Case Study – Lithium-Ion Batteries in China:
With market shares of electric vehicles projected to boom, so will the demand for battery cells. Chinese
battery manufacturers have been observed to be expanding tremendously. In 2017, Forbes reported
that there were more than 140 battery manufacturing companies in China, that had increased their
manufacturing capacities to reach 125 GWh, thereby doubling their capacities within a mere three
years. This capacity is expected to double by 2020, thereby taking up 70% of battery cell market share
(Perkowski 2017). This is partially attributed to a massive increase of production of Chinese electric
vehicles, connected with the preference of Chinese producers of vehicles to use domestically
produced lithium-ion batteries.
As the end of life of the electric vehicles that China started to push for in 2009 is approaching, lithium-
ion batteries, containing heavy metals and other toxins which are potentially harmful to human health
and the environment are expected to pile up. Recycling the batteries is meant to be the burden of the
manufacturer, though plenty of informal enterprises have taken it upon themselves to perform recycling
processes in their backyard. Nevertheless, recycling of lithium-ion batteries is supposedly not very
profitable unless undertaken in large quantities (Stanway 2017).
While the Chinese government aims at transforming battery recycling industry into a high-tech and
highly regulated branch, a growing number of (largely informal) refurbishes is bridging the time it takes
by repurposing old – but still working batteries either into either new applications or for power storage.
Picking up on this trend, the BMW AG plans to test an energy-storage farm to capture energy
generated from renewable sources based on up to 700 used battery packs (Minter, 2018).
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For road traffic, air pollution through particulate matter and sulfur emitted by diesel motors is one of the
largest concerns from a human health and environment perspective. In this regard, a shift in all countries
towards low-sulfur fuels and the establishment and implementation of emission control regulations
and/or action plans will be necessary to reduce the negative effects of the diesel fleet (UN Environment
2017). To reduce air pollution from the transport sector, WHO (2018) suggests shifting to clean modes
of power generation, to improve public (rail) transportation within and between urban areas, provide
incentives for walking and cycling in cities, as well as a shift towards cleaner heavy-duty diesel vehicles
with lower emissions. Furthermore, fuels with lower sulfur content could contribute to fewer emissions
from fuels (ibid.).
In how far the trends of increased interconnectivity and autonomous driving will affect the health issue
of transport accidents and injuries remains to be seen. Recent tests of autonomous vehicles have shown
that accidents tend to increase with the mileage driven, not unlike conventional cars (Favarò et al. 2017).
Meanwhile, a shift towards electric vehicles, though probably leading to reductions in noise and
improvements of air quality, may have other adverse effects if current problems of battery recycling are
not solved.
2.5.3. Opportunities for sustainable chemistry innovation
Disruptive changes in the automotive / transportation sector will also have changing effects on the
market that manufactures the chemicals and materials built in or used for vehicles. Deloitte (2018)
expects a shift away from the production of lubricants, automotive fluids, or fuel additives, particularly
due to the move away from the combustion engine. Not only will the single-gear electric motor consist
of far fewer moving parts, which will require less diverse materials, and fewer lubricants and other liquids,
but instead it will lead towards an increased demand for battery materials (e.g. lithium and copper). To
maximise energy-usage, light-weight materials such as high-performance polymers and commodity
polymers are expected to be built in future vehicles (ibid.). Often as compound materials which are
Case study – The waste legacy of lead-acid batteries:
One contemporary issue with combustion motor vehicles is their use of lead-acid batteries. While
about 85% of all lead goes into lead-acid battery production, application in conventional vehicles is
their primary use (International Lead Association 2012). Recycling those lead-acid batteries (ULAB) is
a highly polluting procedure. Globally 1.9 million people are at risk from severe health damages from
lead exposure due to unsound lead-acid battery recycling (Pure Earth; Green Cross 2016, Daniell et
al. 2015). The often informal operations in many low- and middle-income countries pose severe health
risks especially to children (The Ecologist 2016; Haefliger et al. 2009)-, thus implying a high burden of
disease predominantly in Southeast Asian countries, but also in China (Kuijp et al. 2013), Africa, and
Latin America.
The growing market for automobiles in low- and middle-income countries is expected to also lead to
increasing numbers of lead-acid batteries. It is estimated that more than 1.2 million batteries are put
on the market in Africa each year (Tür et al. 2016). While contemporary electric vehicles use a different
technology, lithium-ion batteries will pose a quickly growing environmental and health challenge in
coming decades, with their own specific recyclability challenges (Lv et al. 2018), in particular the very
diverse mix of compounds that is not easily separated (Gaines 2014). Therefore, innovation must be
fostered not only to develop cheaper batteries with higher capacities, but also to design them to be
more sustainable throughout their life-cycle, with a special focus on their end of life and recyclability
(Larcher;Tarascon 2015)
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difficult or impossible to re-use or recycle, hence posing a contradicting challenge in terms of
sustainability.
Since autonomous driving vehicles are expected to decrease the number of accidents (though, as
mentioned above, these vehicles at their current state do not necessarily confirm this expectation), the
demand for refinishing equipment and eventually even some safety-related equipment may decrease in
future (Deloitte 2018). At the same time, autonomous vehicles may require different coating technologies
and materials, to increase visibility of the vehicles' sensors. The switch away from gasoline towards
electricity will require substantial changes in the supporting infrastructure (gas stations, pipelines), as
well as in the petrochemical industry (ibid).
However, automotive is not the only transportation sub-sector that will undergo a development in terms
of chemical usage. According to several chemical producing enterprises (BASF, Arkema, among
others), light-weight materials and battery solutions also find greater application in the aviation and mass
transportation sectors.
Case study – Metal-Air Batteries:
In order to speed up and facilitate the transition from fossil-fuel based combustion motor vehicles
towards electric vehicles (preferably using energy from renewable sources), manufacturers are in need
of improved energy-storage technologies. Batteries with a high energy density and electronic efficiency
are and will be crucial in this regard. Currently, lithium-ion batteries dominate the market due to “their
high gravimetric and volumetric capacity as well as good energy efficiency” (Liu et al. 2017:246). While
research on improving lithium-ion batteries continues, to make them applicable also in electric vehicles
of high power and energy density, other scientists have taken it upon themselves to investigate
alternatives. One such alternative branch are metal-air batteries which (depending on their sub-type)
do not only consist of materials that are abundantly found on earth, but that also have properties of
high energy density and capacity, the fact that their capacity does depend less on operating load or
temperature, as well as their constant discharge voltage. Depending on their predominant material
(lithium, sodium, potassium, zinc, magnesium, aluminum, iron), they show theoretical energy densities
of up to 10 times that of lithium-ion batteries. Studies on iron-air batteries have shown a performance
of volumetric energy density of nearly five times that of current lithium-ion batteries (9,700 Wh/l
compared to 2000 Wh/l) (Forschungszentrum Juelich 2017).
Despite their promising properties, development of metal-air batteries is still in its infancy, faced with
different issues that, among others, pose safety concerns or negatively affect the reversible charging
and cycle life (Liu et al.). For iron-air batteries, Forschungszentrum Juelich (2017) expect a long way
until they reach market maturity: “Although isolated electrodes made of iron can be operated without
major power losses for several thousand cycles in laboratory experiments, complete iron-air batteries,
which use an air electrode as the opposite pole, have only lasted 20 to 30 cycles so far”.
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2.6. Electronics
2.6.1. Status and forecast of the sector
The electronic sector is a dynamically growing market. According to the German Electrical and
Electronic Manufacturers’ Association (ZVEI 2017), global production of electrical and electronic (E&E)
products was 4,008 billion € in 2015, up 14.5% from 2014, and the industry employed about 27 million
people. ZVEI estimates that by the end of 2018, the market will have grown to 4.5 trillion €. The top
producing regions and their respective market share were:
1. Asia: 2,924 billion € (share: 73%)
2. America: 495 billion € (12%)
3. Europe: 558 billion € (14%)
Closing in on individual countries, the top seven producers, their output and market share are:
1. China: 2,034 billion € (share: 51%)
2. USA: 395 billion € (10%)
3. Japan: 273 billion € (7%)
4. Korea: 245 billion € (6%)
5. Germany: 137 billion € (3%)
6. Taiwan: 98 billion € (2%)
7. Malaysia: 55 billion € (1%)
More than half of the global E&E production takes place in China, though India's manufacturing base is
gearing up and could reach 104 billion US$ by 2020, currently growing at a CAGR of 27%. If consistent,
such a strong CAGR means the sector could double within 3 to 4 years. Looking into the subsectors,
ZVEI (2017) gives the following figures for the individual market segments that together make up the
electrical and electronic products sector (see Table 7).
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Table 7: Size of sectors on electrical and electronic products, market share, and projections. Source: ZVEI
(2017); own calculations.
Sector 2015, in billion € Share in % Projected size in
2018, in billion €
Automation 493.4 12.3 549.7
- Electric drives 125.4 3.1 141.3
- Switchgears, Indus. Control Equipment 173.9 4.3 193.7
- Measurement & Process Automation 194.2 4.8 216.3
Power Engineering 240.1 6.0 262.3
Medical Engineering 95.4 2.4 113.6
Communications Technology 431.0 10.8 466.3
Information Technology 415.0 10.4 449.0
Household Appliances 236.3 5.9 273.5
Lighting 112.0 2.8 126.0
Consumer Electronics 224.4 5.6 245.2
Electronic Components & Systems 977.4 24.4 1,082.8
In almost all electrical and electronic products, chemicals and chemistry knowledge are essential. bcc
research (2016) estimated that the global electronic chemicals and materials market had a value of 22.0
billion US$ in 2014 and was expected to grow to 30.5 billion US$ by 2020.
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2.6.2. Potential concerns from a human health and environment perspective
Manufacturing electronics requires the use of many different chemicals, many of which are problematic
from a health and environment perspective. In a study commissioned by the Nordic Council of Ministers,
Nimpuno and Scruggs (2011) named the following chemical elements and chemicals as the main
hazardous substances in E&E products:
• Lead
• Mercury
• Cadmium
• Zinc
• Yttrium
• Chromium
• Beryllium
• Nickel
• Brominated flame retardants
• Antimony trioxide
• Halogenated flame retardants
• Tin
• Polyvinyl chloride (PVC)
• Phthalates
The use of hazardous substances is a problem for consumers, yet the highest risk is carried by workers
both during the assembly stage and even more during the waste stage of electronic products (Lundgren
2012). Even if the product itself poses little risk to consumers, workers in manufacturing may be exposed
to hazardous levels of dangerous chemicals. At the end of the life-cycle, the risks resurface again. The
health hazards connected with toxic chemicals especially during informal recycling operations are an
increasingly important issue, as the amount of discarded electronic products continues to grow (Perkins
et al 2014).
Globally, 44.7 million metric tonnes of e-waste were generated in 2016, and this amount is expected to
increase to 52.2 tonnes by 2021 (Baldé et al. 2017). The “Global E-Waste Monitor” differentiates
between six categories of e-waste:
• Temperature exchange equipment /refrigerators, air conditioners etc.)
• Screens
• Lamps
• Large equipment (dishwashers, washing machines etc.)
• Small equipment (toasters, vacuum cleaners etc.)
• Small IT (mobile phones, personal computers etc.)
Of the current e-waste flow, 80%, or 35.8 Mt, is not documented and occurs through informal or illegal
channels. Baldé et al. (2017: 5) note that this is "likely dumped, traded, or recycled under inferior
conditions." A key challenge for reducing risks associated with the end-of-life of electrical and electronic
products is an improved information flow throughout the value chain, for which Scruggs et al. (2016)
propose a global standard. Another key challenge is to equip workers in the informal e-waste recycling
sector with the tools and knowledge necessary to avoid the related health risks (Ohajinwa et al. 2017).
While informal e-waste operations are certainly among the most hazardous occupations (Pure Earth
and Green Cross 2016), exposure to toxic substances is common even in formalized e-waste recycling
in developed countries, which requires according measures to protect workers (Julander et al. 2014).
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2.6.3. Opportunities for sustainable chemistry innovation
To become more sustainable, the electronics sector needs to incorporate circular thinking from the
design stage through the entire life-cycle to the waste stage. If done properly, and if connected with
innovative products which have inherent sustainability advantages (see the case study on LEDs below),
there is an enormous potential for the sector to contribute to achieving the 2030 Agenda.
Innovation case study: LEDs
Having access to artificial light is an essential enabling factor for economic development. Conventional
incandescent light bulbs are easy and cheap to produce, but very energy intensive and have a short
life span. While compact fluorescent lights (CFL) are more energy efficient and last longer, they contain
mercury, which poses a health hazard and makes recycling difficult.
Light emitting diodes (LED) offer energy-efficient lighting with a long life-span and without hazardous
substances. Due to technological advances, LEDs can produce light with a high colour rendering index
(CRI). Apart from LED-based household and public illumination replacing incandescent light bulbs and
CFLs, technological advances of LEDs have enabled thinner screens in the form of organic LEDs,
while more recent innovations include LEDs emitting ultraviolet light.
In the US, it is expected that the electricity use from lighting will fall from about 1,100 kWh to about
500 kWh per household due to the use of more energy efficient lighting by 2050, and high efficiency
gains are likewise expected in the commercial sector (EIA 2018). Globally, lighting accounts for about
20% of global electricity usage. The International Energy Agency estimates that by 2022, energy-
efficient lighting (CFLs and LEDs) will account for 90% of indoor lighting (IEA 2017: 12). The IEA also
calculated for Indonesia that, if current LED adoption rates continue, consumers will save up to 560
million US$ in avoided electricity costs per year. This is possible because the price of LEDs has gone
down significantly, from more than 50 US$ in 2011 to less than 10 US$ in 2016 in the US, and
considerably less in India. Energy savings in these two countries alone amounted to more than 140
TWh (IEA 2016: 101).
Though the energy savings are substantial, and related emission reductions including of mercury from
coal-fired power plants are an additional benefit, LEDs are not without risks when it comes to recycling.
While it may be less dangerous than dealing with used CFLs, there are still a number of hazardous
substances built in LEDs which makes their disassembly and recycling challenging from a health and
environment perspective (Lim et al. 2011). Moreover, the small size and multiple applications of LEDs
are a challenge for recollection. Much improved recollection systems are therefore an indispensable
prerequisite for recycling of their constituents.
Fostering sustainability innovation in the electronics sector would also enable to monetarize a hitherto
largely wasted economic opportunity, as the value of raw materials in all e-waste is estimated to be
around 55 billion US$ (see Table 8).
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Table 8: Mass and value of raw materials in e-waste. Source: Baldé et al. 2017: 54.
Material Kilotons (kt) Million €
Fe 16,283 3,582
Cu 2,164 9,524
Al 2,472 3,585
Ag 1.6 884
Au 0.5 18,840
Pd 0.2 3,369
Plastics 12,230 15,043
2.7. Textiles
2.7.1. Status and forecast of the sector
The world of textiles is well-established, generally sophisticated with a large variety of fibres and
constructions routinely sold and expanding globally in recent years. A view from a high-level perspective
finds both commodity and specialty materials — produced as woven, knitted and nonwoven fabrics in
forms from natural, synthetic, inorganic, including bio-polymer materials — emerging in the last few
decades, serving the needs of the apparel sector as well as various technical sectors (e.g. technical
textiles for constructions, building and living, automotive, medical sectors). With the global population
rising to around 8.5 billion people by 2030 (and even further until 2040) and GDP per capita expected
to grow at 2% per year in the developed world and 4% in the developing world, the overall apparel
consumption is poised to increase by 63%, from 62 million tons (2016/2017) to 102 million tons in 2030
- an equivalent of more than 500 billion T-shirts.
Already, in the last 15 years, worldwide clothing production has approximately doubled (Ellen McArthur
Foundation 2017a) driven by a growing middle-class population across the globe and increased per
capita sales in mature economies. The latter rise is attributed to the ‘fast fashion’ phenomenon, marked
by quicker turnarounds of new styles, increased number of collections offered per year, often lower
prices and a declining cloth utilisation rate. This soaring current and future demand for apparel—much
of it from developing nations—will see the annual retail value of apparel and footwear reach at least
US$ 2.3 trillion by 2030 (an over 30% increase of US$ 590 billion between now and then) (ref. Global
Fashion Agenda and Boston Consulting Group 2017).
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Figure 10: Growth of clothing sales and comparison with declining clothing utilisation.
Source: Ellen MacArthur Foundation 2017: A New Textiles Economy: Redesigning Fashion's Future.
Reprinted with friendly permission of the Ellen MacArthur Foundation.
In line with this development, the chemical intensive textile sector is expected to grow as well.
Accordingly, the growth of global apparel industry drives the development of the textile chemicals
demand over the forecast period. Comparative forecasts from various market research institutions as
well as the chemical industry itself place the prognosticated value of the global market for textile
chemicals market at US$ billion 31.8 by the end of 2026 (from US$ 21.02 billion in 2015), implying a
growth at a rate of 3.7% CAGR over the forecast period, 2016 – 2026 (Transparency Market Research,
Inkwood Research, Grandview Research 2018).
The typical range of products comprises of wetting agents, emulsifiers, dispersants, detergents,
chelating agents, and biocide active ingredients. Increasing demand for technical textile across
numerous end-use applications is also expected to be beneficial for the overall market growth of textile
chemicals. Surfactants are the largest chemical category consumed in textile processing and are used
in many different functional textile formulations and operations as scouring agents, dyebath additives,
and softeners. In 2015, surfactants accounted for close to 30% of the total global value of chemicals,
followed by warp sizes and coatings (IHS Markit 2016) with a total worth of US$ 6.35 billion in 2015.
The Asia Pacific textile chemicals industry is expected to witness the fastest growth and is expected to
grow at a CAGR of 4.2% from 2016 to 2025. Expansion of key textile manufacturing players in the
region, coupled with increasing domestic consumption of novel textile products is expected to support
the region to maintain its dominance over the forecast period. The technical textile application segment
is estimated to witness the fastest growth over the next ten years. For example, the U.S. product market
in this segment is anticipated to grow at a CAGR of 3.8% from 2016 to 2025 to reach a net worth of US$
930.1 million by 2025.
China is likely to remain the world’s largest manufacturer of textiles and apparel. Growing disposable
income among the growing Chinese middle class resulted in increasing consumption, including of
fashion and apparel. In line with these, the Chinese textiles and apparel will focus on meeting the
domestic demand, which is marked by high turn-overs and quickly changing fashion trends. Over the
longer term, macro-employment trends (such as China`s labour pool shrinking by one-fifth over the next
50 years) are expected to weaken China’s manufacturing base (McKinsey Global Institute). Many
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Chinese garment makers have already started opening or sourcing from manufacturing facilities in
Bangladesh, Cambodia, Vietnam, Myanmar, Pakistan as well as in other up-and-coming sourcing
countries, in an effort to tap into lower-cost labour pools and utilise trade agreements to better feed both
the global garment buyers and the domestic market at an appealing price point. Apart from these already
established manufacturing hubs in Asia, Ethiopia is poised to become a fast-growing manufacturing hub
in Africa (McKinsey 2015). With the given demographic changes and economic developments on the
African continent as drivers, the textile and garment industry in Africa may be able to take advantage of
its vicinity to the markets in Europe as well as to a fast growing and large African market. The population
in Africa is expected to reach 2 billion people by 2050, of which 56% will be residing in urban areas
(African Development Bank 2016). In the long run, several other African countries, particularly those
with strong potential for supply chain backward integration (e.g. production of natural fibres meeting the
demand for organic cotton), are expected to expand their garment and textile industry as part of their
national industrialization strategies, hereby considering the sector’s employment opportunities for their
youth population (African Development Bank 2017).
Growing urbanization with a corresponding growth of residential construction and a growing middle class
with disposable income and higher expectations regarding quality life style, particularly in the Asia-
Pacific region and in emerging economies such as China, India, Russia, and Brazil, are expected to
drive the apparel and home textile market (e.g. window shades, towels, toilet and kitchen linen,
coverings, mats, rugs, and textile floors), which holds a dominant market share in the worldwide textile
chemicals market 38.62% in 2015). The rising consumer demand for innovative and styled clothing
products is expected to be a key factor steering the market growth in the coming years.
Under a business-as-usual scenario, these sector developments will have significant environmental
implications at the existing as well as emerging manufacturing locations. the World Bank estimates that
20% of industrial wastewater pollution worldwide originates from the textile industry. (Kant 2012: 23). In
addition to waste water, textile production contributes to chemical containing solid wastes, sludge as
well as air emissions (IFC 2007). However, growing environment and health concerns regarding the
adverse effects of chemicals, , have emerged as a major factor in the overall market development - not
only in markets such as the USA and Europe. Apart from the consumers’ concern for potentially harmful
chemicals in final products and their possible negative impacts during use, the scope has expanded to
the whole value chain over the last 15 years. Sensibilitation campaigns, such as the Anti Fast Fashion
Movement or the Detox Compaign launched by Greenpeace in 2011, with the aim of reaching a toxic-
free production by 2020 by eliminating 11 priority chemical groups (ECHA 2017), created additional
public pressure on the different players in the value chain, including the suppliers of textile chemicals.
2.7.2. Potential concerns from a human health and environment perspective
Of the total fibre input used for clothing, 87% is landfilled or incinerated. During the period 2010 to 2015,
the volume of sales has doubled from around 50 bn units to more than 100 bn units. At the same time,
the clothing utilisation rate (average rate of a unit being used before it ceases to be used) has steadily
dropped. This ‘take-make-dispose’ system (“fast fashion”) is not only extremely wasteful on resources,
but also very polluting (Ellen MacArthur Foundation 2017a). Less than 1% of material used to produce
clothing is recycled into new clothing, representing a loss of more than US$ 100 bn worth of materials
each year. Current practices contribute to around annually 0.5 million tonnes of microfibre leakages into
the oceans. Under a business-as-usual scenario, the growth in material volume of textiles would see an
increasing amount of non-renewable inputs, up to 300 million tonnes per year by 2050. On current trend,
the amount of plastic microfibres entering the ocean between 2015 and 2050 could accumulate to an
excess of 22 million tonnes – about two thirds of the plastic-based fibres currently used to produce
garments annually (Ellen MacArthur Foundation 2017a). The new textiles economy would strive for a
combination of (1) phasing out of substances of concern and microfibre releases, (2) increasing clothing
utilisation, (3) radically improving re-/upcycling and (4) making effective use of resources and (5) moving
to renewable inputs (e.g. renewably sourced feedstocks for fibres).
Though the overall economic benefits of phasing out substances of concern might be difficult to assess
due to low transparency on chemical use or data on worker-related health impacts, it is estimated that
eliminating today’s negative health impacts emanating from poor chemicals management in the textile
industry would have an economic benefit of 7 billion € (8 billion US$) annually in 2030. (Global Fashion
Agenda; Boston Consulting Group 2017) The potentially negative impacts extend beyond the production
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of fibres and textile (e.g. use of pesticides during cotton growing) and the use of clothing (e.g. release
of substance during washing). 73% of clothing ends up in landfill or is incinerated at their end of life. The
Swedish Chemicals Agency (KEMI) estimates that substances of concern contained in textiles, such
as any remaining dyes or chemicals introduced during production or use, can leak from the textiles as
they degrade, accounting for the release of over 2,000 tonnes of hazardous colourants in the EU each
year. If waste is incinerated without controlling emissions, the combustion gases also have the potential
to release substances of concern. (KEMI 2014)
The environmental impacts of this product are significant, since the fibre and textile production is both
water and chemical intensive. For example, to produce a single t-shirt it takes around 2700 litres of
water. At the same time, the process generates large volumes of waste water, containing residuals of
chemicals not absorbed by the material manufactured.
2.7.3. Opportunities for sustainable chemistry innovation
Stringent environmental regulation, growing restrictions on specific chemicals/chemical groups in whole
value chains by international buyers, campaigners (e.g. the DETOX campaign by Greenpeace) or
industry driven initiatives such as Zero Discharge of Hazardous Chemicals (ZDHC), blue signs as well
as the wider consideration of circular economy concepts drive the changes and innovations in the textile
and apparel sector. Leading brands as well as young start-ups are increasingly offering "green", “bio”
and “sustainable" collections, which emphasize aspects such as avoidance of toxic chemicals, use of
recycled or upcycled fibres, low water and carbon footprints as well as end-of-life recyclability (Ellen
MacArthur Foundation 2017a). There has been an increase in popularity of sustainable textile fibres,
which includes organic cotton, flax, hemp, jute, sisal, abaca, and bamboo. Renewable and
biodegradable synthetic fibres manufactured from natural resources such as polylactic acid and lyocell
are being preferred over petroleum-based non-biodegradable synthetic fibres such as polyester
(Technavio Research 2017)
These developments have already fostered new forms and closer cooperation between manufacturers,
researchers and chemical suppliers over the last years to address the environmental as well as
safety/health impacts through innovations in process technologies and textile chemicals. Low-water
consuming (low float technologies) and even water-free production technologies (e.g. water free carbon
dioxide-based dyeing, DyeCoo, Netherlands) are increasingly being adopted by manufacturers in the
textile segment as Best Available Technologies (BAT). Textile chemical suppliers are responding by
aligning their textile chemical portfolios with the emerging positive and negative lists of chemicals,
developing less-and low hazard alternatives, with reduced water usage and effluent discharge (e.g. salt-
free dying solution which reduce the discharge of Total Dissolved Solids TDS or Salt-free reactive dyeing
of cotton hosiery fabrics by exhaust application of cationic agent, Journal of Cleaner Production 2016:
1-11) as well as guiding their customers in the effective use of these chemicals and sound chemicals
management. Emerging manufacturing hubs ( in particular in Africa) start to adapt and integrate such
best available and appropriate technologies, to address potential conflicts about resources (e.g. use of
arable land for growing food crops or natural fibres, use of ground and surface water for industrial
production or agricultural and domestic use), thereby avoiding the mistakes in established
manufacturing hubs.
In response to market trends, the textile industry itself is moving ahead with the development of new
textile materials and fabrics, incorporating smart functions into the fabrics, using nano- and
biotechnology know-how, sensory functions, wearable electronics and Internet of Things. In addition to
enhanced functionalities, R&D and innovations in products aim at increasing comfort, wellness,
freshness, and care.
Industry 4.0 with new technologies and methods are beginning to change and disrupt the traditional way
of textile/apparel production as well. Combining new developments in automatization (e.g. robotic and
additive manufacturing) with material sourcing and material science, digitalisation in value chains will
have widespread implications on the textile and apparel industry in those countries which presently rely
on plentiful availability of human resources and low costs (ILO 2016). Such automated production units
have already started operations (Example: The Adidas Speedfactory). Automation will enable greater
decentralization and flexibility in global manufacturing. It signals potential job losses for textile hubs like
Bangladesh due to “insourcing” to advanced economic countries as well as easier relocation to new
emerging markets (Centre for Policy Dialogue 2016; 2018). At the same time, how consumers view
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fashion has begun to change. The idea of slow fashion is making inroads, which not only advocates
buying less and focusing on quality over quantity but also putting increasing emphasis on the
sustainability aspects of product and production.
Taking into consideration the sector`s developments, concerns as well as opportunities, following key
innovation areas for sustainable chemistry in the textile sector emerge: (1) Development of new
materials (such as synthetic and cellulosic fibres), (2) development of new safer textile chemicals (such
as safer finishing chemicals and bio-based dyes), (3) contribution to reducing water consumption for
example into the direction of waterless processing (e.g. waterless dyeing and finishing processes) as
well as water reuse, (4) advancing scope for fibre recycling (e.g. cotton, polyester, blends and nylon),
(5) establishment of supportive systems (e.g. chemicals management information systems, traceability
systems). (Fashion For Good; Safer Made 2018) and (6) water treatment and recycling towards closed
loops (e.g. advanced water treatment and recovery, recovery of chemicals).
Summary of key disruptors
• Product customization technology, such as additive manufacturing, body scanners and
computer-aided design (CAD),
• Computerised manufacturing processes, namely automated cutting machines and sewbots
• Wearable technology, nanotechnology, and
• More sustainable, environmentally friendly manufacturing techniques
• Recyclability of materials and products
2.8. Pharmaceuticals
2.8.1. Status and forecast of the sector
Universal health coverage is one of the targets the nations of the world have adopted in the Sustainable
Development Goals (SDGs). And it’s also a top priority of the WHO as part of the organization’s „Health
For All“ strategy. Ultimately, countries that make progress toward universal health coverage don’t just
achieve better health outcomes for their people. They also will progress toward the other health-related
targets and SDGs. Better health allows children to learn and adults to earn; it helps people escape from
poverty; and it lays the foundation for long-term economic development. Health is a fundamental and
universal human right. No one should get sick or die just because they are poor or because they cannot
access the medicines or technologies they need. And access to pharmaceuticals and other health
technologies—vaccines, diagnostics, medicines, medical devices and assistive technologies—is a key
pillar of universal health coverage (WHO 2017).
In 2016 North America accounted for 49.0% of world pharmaceutical sales compared with 21.5% for
Europe. According to IMS Health data (QuintilesIMS 2016), 64.7% of sales of new medicines launched
during the period 2011-2016 were on the US market, compared with 17.5% on the European market
(top 5 markets). There is rapid growth in the market and research environment in emerging economies
such as Brazil, China and India, leading to a gradual migration of economic and research activities from
Europe to these fast-growing markets. In 2016 the Brazilian and Chinese markets grew by 10.0% and
6.9% respectively compared to an average market growth of 4.5% for the total European Union market
and 6.3% for the US market.
The total volume of medicines consumed globally will increase by about 3% annually through 2021
(QuintilesIMS 2016), only modestly faster than population and demographic shifts, but driven by very
different factors around the world. Spending on medicines will grow by 4–7%, primarily driven by newer
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medicines in developed markets and increased volume in emerging markets. Developed markets will
offset increased costs from new medicines with the use of generics, and a greater focus on pricing and
access measures, while emerging markets will struggle to live up to promised access expansions made
when their economic outlooks were stronger.
Global medicine spending will reach nearly $1.5 trillion by 2021, up nearly $370 billion from the 2016
spending level. Most global spending growth, particularly in developed markets, will be driven by
oncology, autoimmune and diabetes treatments where significant innovations are expected. The U.S.
will continue as the world’s largest pharmaceutical market and emerging markets will make up 9 of the
top 20 markets. China will continue as the second largest market, a rank it has held since 2012.
Developed market spending growth will be driven by original brands, while emerging markets will
continue to be grow through non-original products that make up an average 91% of emerging market
volume and 78% of spending. Global spending of new medicines will continue to rise from less than
20% in ten years to 35% by 2021 , approaching half of total spending in U.S. and European markets.
This rise primarily will be driven by the adoption of new breakthrough medicines, but also will be a key
focus of payers and constrained by cost and access controls as well as a greater focus on assessments
of value. Off-invoice discounts and rebates, particularly in the U.S. market, will reduce growth by about
1%, resulting in a total global market of $1 trillion in 2021.
The number of new medicines reaching patients will be historically large with 2,240 drugs in the late-
stage pipeline and an expected 45 new active substances (NAS) forecast to be launched on average
per year through 2021. The new medicines will address significant unmet needs in cancer, autoimmune
diseases, diseases of the metabolism, nervous system and others. In addition to the continued research
of mechanisms in use in existing drugs, there will be an ongoing flow of new mechanisms to target cell
processes and diseases across the spectrum. Developments that go beyond specific “drugs” are
emerging in research that will challenge traditional regulatory approval and commercialization
approaches. These include completely new platforms that will see their first human uses in areas such
as gene-editing technology CRISPR, which could transform personalized cancer treatments while
creating a plethora of ethical dilemmas. Advances are expected to treat a range of diseases by
harnessing the microbiome (a person’s own gut bacteria), as well as regenerative cell technologies that
include stem cells harvested from one part of the body to use against a disease in another.
Cancer is by far the largest general category of research, including immunology, cell-therapy and dozens
of molecularly targeted agents. Treatment choices will be made based on the tumor diagnosis as much
as by a patient’s family history, genetic marker or by biomarkers the tumor expresses. The sheer number
of cancer treatments, their potential combinations in treatment regimens, and the variety of companies
involved in development will bring significant change to the landscape of cancer treatment over the next
five years. Dramatic improvements in survival and tolerability are expected and will be accompanied by
substantially greater levels of clinical trial and real-world information to support treatment decisions.
Payers and providers are developing tools to better assess value and will demand, or create on their
own, the evidence to support spending, especially where new treatments would add to already
expensive cancer treatment costs.
2.8.2. Potential concerns from a human health and environment perspective
Pharmaceuticals can enter the environment at all stages of the product’s life-cycle. The major source of
pharmaceuticals entering into the environment is via excretion, following the use of a medicine taken to
prevent, cure or alleviate a medical condition. A comparatively smaller contribution stems from industry
emissions during the manufacture of pharmaceuticals and from the incorrect disposal of unused or
expired medicines.
The issue of pharmaceuticals in the environment requires a balanced approach. In contrast to many
other substances/chemicals in the environment medicines play an important role in human health.
Today, citizens can expect to live up to 30 years longer than they did a century ago. Huge reductions in
mortality (e.g. from HIV/AIDS, many cancers or cardiovascular disease) and significant progress in
terms of quality of life are the results of some large and many small steps in biopharmaceutical research
(IFPMA 2017). The public health benefits of pharmaceuticals should always be the priority when
assessing the environmental impact of pharmaceuticals.
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Addressing potential risks of pharmaceuticals in the environment requires a sound assessment of
current and future actions, whilst remaining mindful of patient needs and ensuring access to medicines.
Founded on the principles of product stewardship, the ECO-Pharmaco-Stewardship (EPS) initiative has
been developed (EFPIA 2016). It considers the entire life-cycle of the medicine and addresses the roles
and responsibilities of all parties involved, including public services, the pharmaceuticals industry,
environmental experts, doctors, pharmacists, and patients. The EPS initiative is supported by three
pillars, which have been identified as key areas of focus for the pharmaceutical industry:
Pillar 1 – Identification of the potential environmental risks of existing and new active pharmaceutical
ingredients (API) through intelligent and targeted assessment strategies. The European pharmaceutical
industry has initiated a project under the Innovative Medicines Initiative (IMI), a joint undertaking
between the European Commission (EC), academia and the pharmaceutical industry. The project will
use all available scientific knowledge to develop tools and assays, which will prioritise and identify the
pivotal areas in which more data would strengthen the understanding of a potential risk for medicinal
products in use today. This will enable the most efficient and effective use of resources. It is anticipated
that the output may also be applied to screen new active pharmaceutical ingredients in development to
target environmental testing needs. Studies such as these are the prerequisites and must inform the
implementation of measures that increase sustainability in pharmaceutical development and
consumption.
Pillar 2 – Manufacturing effluents management: the compilation of best industry practices, enabling
manufacturers to minimize risks to the environment. For the most part, the processes used to
manufacture medicinal products are largely similar wherever in the world they may be used. It therefore
follows that potential losses into the environment from manufacturing facilities should also be equally
controllable. However, this assumes that a good understanding of the risk to the environment and the
knowledge required to limit losses are uniformly available. In an effort across the industry, experts from
several major manufacturers have shared experiences and developed a “maturity ladder” and
associated guidance, in order to enable an enhanced understanding of the existing methods and the
potential need for specific methodologies relative to the potential environmental risk posed by APIs
and/or manufactured medicinal products. Manufacturing companies were encouraged to exchange
practices in further developing their level of effluent control systems.
Pillar 3 – extended ERA: the refinement of the existing environmental risk assessment (ERA) process
for medicinal products to ensure that they remain up-to-date and relevant. An important cornerstone of
EPS is a refined Environmental Risk Assessment (ERA) process, extending beyond marketing
authorization. The ERA of a medicinal product is currently performed by companies either as part of a
new marketing authorization or when an increase in the environmental exposure is expected, e.g. with
the approval of a new indication or the inclusion of a new patient population. ERA must be performed to
evaluate potential risks of medicines to the environment and ensure adequate precautions are taken
where specific risks are identified. The extended ERA (eERA) includes provisions to:
(i) adjust exposure predictions as usage figures become available to better reflect reality, including all
products with the same API; and (ii) reconsider the effects profile, as relevant and reliable laboratory findings and/or observations in the
field linked to an adverse outcome become available. The need for diligence does not end with the EPS pillars; there are many other opportunities to
minimize losses to the environment along the life-cycle of a medicinal product, such as increasing
transparency and access of the environmental data, and educating the public on the correct use and
disposal of unused and expired medicines. In order to promote the latter, a collaborative campaign
focusing on the correct disposal of unused and expired medicines was initiated by the industry in 2015
(EFPIA 2016).
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2.8.3. Opportunities for sustainable chemistry innovation
Overview of possible actions to further curb the impact of pharmaceuticals in the environment:
➢ More research to better understand the risks;
➢ More stringent conditions for putting a pharmaceutical on the market;
➢ „Greener“ design of pharmaceuticals, e.g. to make them more biodegradable;
➢ Cleaner manufacturing;
➢ Better risk mitigation, e.g. not allowing over-the-counter sale of pharmaceuticals that pose an
environmental risk;
➢ More thorough post-market monitoring of pharmaceuticals in the environment and feedback to the
regulatory process;
➢ Better training for medical professionals, e.g. about pharmaceuticals that are less harmful for the
environment;
➢ Better information for the public, e.g. about how to dispose of unused medicines;
➢ Smaller packaging sizes, to reduce unnecessary waste/disposal;
➢ Improved handling of waste pharmaceuticals;
➢ Improved sewage and wastewater treatment;
➢ Improvements in livestock farming to reduce the use/emission of pharmaceuticals.
Some emerging areas and fields of innovation
The pharma industry is at the early stages of a fundamental shift as advanced data sciences are
embedded across the value chain. For the last four decades, the volume and variety of medical
innovation has expanded significantly, a trend driven in large part by continued innovation and large-
scale utilization of electronic medical records, high-resolution medical imaging, and next-generation
genomics. Pharmaceutical companies have begun to realize benefits from this evolving data ecosystem,
using new methods for rapid acquisition, curation, analysis, and visualization of large, diverse data sets
in cloud-based storage and distributed computing power platforms (BCG 2017, Deloitte 2018, McKinsey
2018).
➢ Artificial Intelligence & Machine Learning: Artificial Intelligence (AI) is the simulation of human
intelligence processes by machines, especially computer systems. Drug/biotech companies are
analyzing the huge amount of data in their database by applying artificial intelligence and machine
learning to identify patterns in ways that humans cannot. Artificial intelligence driven solutions are
enabling pharma/biotech companies to identify the appropriate patient population, reduce or
eliminate the need for some studies, and in some cases even predict outcomes in a virtual patient.
Several collaborations have been formed in the past couple of years between big pharma/biotech
players and AI-driven companies, primarily start-,ups to discover novel biological targets and
molecules for pharma players using AI. Medical decision made with artificial intelligence using the
power of supercomputers will revolutionize everyday medicine. Cognitive computers, such as IBM
Watson, have been used in many ways to analyze big data, not only in genomic research but also
in biotechnology. This will change the way new drugs are found as a machine can analyze with
greater accuracy and speed.
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➢ Genomics & Personalised Medicine: Genomics enables patients to receive therapy individually
customized to their genetic background. Patients will own a huge text file containing their DNA data.
They can take it to their doctor and receive personalized drugs instead of the blockbusters that are
manufactured for millions of people even though patients are all genetically and metabolically
different. The cost of DNA sequencing is dropping constantly. When it’s finally available to the
majority the whole concept of prescribing medication will change. Pharmaceutical companies need
to get ready for the transformation, so it can offer solutions to all.
➢ Internet of Medical Things (IoMT): Internet of Medical Things brings together medical devices and
applications and technology that procure vital data in real time. Chronic diseases, which require
frequent monitoring, can be tracked effectively so that patients receive timely and proper treatment.
Wearable devices like Apple Watch, Fitbit and Samsung S Health help users achieve their fitness
and health targets. It could well be the future of healthcare as pharma and medical device
companies look to innovate and keep up with technology to help patients and physicians better
monitor and track diseases (Allied Market Research 2016). Pharma and tech companies are now
taking things a step further and collaborating to make devices that can track chronic and lifestyle
associated diseases like diabetes, which are becoming rampant. In fact, the scope for innovation in
this area — contact lenses that can detect glucose levels, devices that monitor caloric intake,
bioelectronic medicines that may treat a wide range of chronic diseases, robotic-assisted surgery
— is seemingly endless.
➢ 3D Bio-Printing: Three dimensional printing or 3D printing is a prototyping technology by which
different materials are fused under computer control to create a three-dimensional object. Add
biology/cells to the process and it becomes a new technique – 3D bioprinting. These printers are
used to manufacture human tissues/muscles as well as organs and bones that can be implanted
into living humans. 3D printing technology, also known as additive manufacturing, is leading to major
innovations in medicine manufacturing, particularly personalized medicines. Compared to
conventional manufacturing systems, 3D bioprinters offer benefits like high production rates, better
precision and accuracy and reduces material wastage, which can save costs. Though still new to
pharmaceutical drug research and development, 3D printing has been in use in the medical devices
sector for many years. A Scottish group has been working on printing out drugs in 3D with a printer.
The first drug printed out with a 3D printer was approved by the Food and Drug Administration (FDA)
in 2015. In future, patients can get a blueprint of a customized drug in a customized dosage related
to their genomic background and a local pharmacy will print it out for them without the participation
of a pharmaceutical company.
➢ Nanorobots: In blood nanorobots could make early diagnoses by constantly measuring any health
parameters. If the technology of transporting drugs to the actual cellular targets in nanocarriers
becomes viable, the pharma industry will have to start producing different end products to make
sure they are compatible with nanotechnology. This requires a new approach to medication, without
which the transformation of pharma could be a hard and rocky one. This is the most futuristic
example, but it’s never early enough to start preparing for a new revolution.
Foundational Paper by the International Sustainable Chemistry Collaboration Centre for the GCO II
47 May 2018
3. List of Abbreviations
AI Artificial intelligence
API Active pharmaceutical ingredients
BAT Best available technology
Btu British thermal unit
CAD Computer-aided design
CAGR Continuous annual growth rate
CAS Chemical Abstracts Service
CEEC Center for Energy and Environmental Chemistry
CFL Compact fluorescent light
CRI Colour Rendering Index
EC European Commission
EIA Electronic Industries Alliance
E&E Electrical and electronic products
EPR Extended Producer Responsibility
EPS Eco-pharmaco-stewardship
ERA Environment Risk Assessment
EU European Union
EV Electric vehicle
FAO Food and Agricultural Organisation of the United Nations
FDA Food and Drug Administration
GDP Gross domestic product
GERD Gross domestic expenditure on research and development
GHG Greenhouse gas
IEA International Energy Agency
IFA International Fertilizer Association
IFC International Finance Corporation
ILO International Labour Organization
IMI Innovative Medicines Initiative
IoMT Internet of medical things
IRENA International Renewable Energy Agency
LED Light emitting diode
MNC Multinational Corporations
NAS New active substances
NGO Non-Governmental Organisation
NUE Nitrogen use efficiency
OECD Organisation for Economic Co-operation and Development
PCT Patent Cooperation Treaty
Foundational Paper by the International Sustainable Chemistry Collaboration Centre for the GCO II
48 May 2018
PPP Purchasing power parity
PV Photovoltaic
R&D Research and development
ULAB Used lead-acid batteries
UNEP United Nations Environment Programme
UNESCO United Nations Educational, Scientific and Cultural Organisation
UNRISD United Nations Research Institute for Social Development
SDGs Sustainable Development Goals
SEIA Solar Energy Industries Association
SPV Solar photovoltaic
SVHC Substances of very high concern
SVOC/VOC Semi volatile organic compounds/Volatile organic compounds
TDS Total dissolved solids
VCI Verband der chemischen Industrie
WBCSD World Business Council for Sustainable Development
WEEE Waste Electrical and Electronic Equipment
WHO World Health Organisation
WIPO World Intellectual Property Organisation
ZDHC Zero Discharge of Hazardous Chemicals
ZVEI Zentralverband Elektrotechnik- und Elektroindustrie e.V.
Foundational Paper by the International Sustainable Chemistry Collaboration Centre for the GCO II
49 May 2018
4. List of Figures and Tables
Figure 1: 40 key and emerging technologies. 12
Figure 2: Patent grants on chemicals-related innovations across regions. 13
Figure 3: PCT patent publications on chemicals-related technologies. 13
Figure 4: Number of chemical substances registered with the Chemical Abstracts Service
(CAS). 14
Figure 5: Global population living in urban and rural areas. 1950 -2014-2050 (projected) 17
Figure 6: Growth of urban population by city size. Source: UNDESA 2017b. 18
Figure 7: Energy-related CO2 emissions per capita. 19
Figure 8: Change in world primary energy demand by fuel. 27
Figure 9: Number and share of people without access to electricity by country, 2012. 28
Figure : Growth of clothing sales and comparison with declining clothing utilisation. 39
Table 1: Matrix analysis of megatrend studies 8
Table 2: Gross domestic product of the world's 10 largest economies, in constant 2010 US$.9
Table 3: Projected share of global GDP (PPPs) in 2016 and 2050. 10
Table 4: Global chemical shipments by region. 10
Table 5: Past and projected share of chemical sales across regions. 11
Table 6: World Population Prospects. 16
Table 7: Size of sectors on electrical and electronic products, market share, and projections.
Source: ZVEI (2017); own calculations. 35
Table 8: Mass and value of raw materials in e-waste. Source: Baldé et al. 2017: 54. 38
Foundational Paper by the International Sustainable Chemistry Collaboration Centre for the GCO II
50 May 2018
5. Bibliography
Adams, K. T.; Osmani, M.; Thornback, J. (2017): Circular Economy in Construction: Current
Awareness, Challenges and Enablers. Waste and Resource Management, 170(1), 15-24.
African Development Bank (2016): African Economic Outlook 2016: Sustainable Cities and Structural
Transformation.
African Development Bank (2017): African Economic Outlook 2017: Entrepreneurship and
Industrialisation.
Agarwal, R.; Chandrasekaran, S.; Sridhar, M. (2016): Imagining construction’s digital future.
McKinsey, https://www.mckinsey.com/industries/capital-projects-and-infrastructure/our-
insights/imagining-constructions-digital-future, accessed 9 May 2018.
Amato, I. (2013): Green Cement: Concrete Solutions. Nature, 494 (7437)
American Chemistry Council (2017): 2017 Elements of the business of Chemistry. Washington DC,
American Chemistry Council.
Andrew, R. M. (2018): Global CO2 Emissions from Cement Production. Earthy System Science Data,
10, 195-217.
A.T. Kearney (2012): Chemical Industry Vision 2030: A European Perspective.
Bahadur, S. (2017): Sustainable architecture is the future. Chemical Today Magazine, March 2017,
26-28.
Baldé, C. P.; Forti, V.; Gray, V.; Kuehr, R.; Stegmann, P. (2017): Global E-waste Monitor 2017.
Bonn/Geneva/Vienna: United Nations University (UNU), International Telecommunication Union (ITU);
International Solid Waste Association (ISWA).
Bcc research (2016): Electronic Chemicals and Materials: The Global Market.
BMU (2018): GreenTech Made in Germany 2018. Umwelttechnik-Atlas für Deutschland. Berlin:
Bundesministerium für Umwelt, Naturschutz und nukleare Sicherheit.
British Petrol (2013): Energy Outlook 2030, www.bp.com/content/dam/bp/pdf/energy-
economics/energy-outlook-2015/bp-energy-outlook-booklet_2013.pdf
Bren d’Amour, C.; Reitsma, F.; Baiocchi, G. et al. (2016): Future Urban Land Expansion and
Implications for Global Croplands. PNAS, 2017. 114 (34) 8939-8944.
CEFIC (2017): Facts and Figures: The European Chemical Industry 2017. Brussels.
CEFIC (2018): Landscape of the European Chemical Industry 2018. Brussels.
Centre for Policy Dialogue (2016): CPD RMG Study 2016, Bangladesh http://rmg-study.cpd.org.bd/,
accessed 10 May 2018.
Centre for Policy Dialogue (2018): Dialogue on “Ongoing Upgradation in RMG Enterprises: Results
from a Survey” held on March 3, 2018, http://cpd.org.bd/wp-content/uploads/2018/03/Ongoing-
Upgrdation-of-RMG-Enterprises.pdf, accessed 10 May 2018.
Coherent Market Insights (2016): Distributed Generation Market, By Technology, By Application,
by Enduser, by Geography – Global Industry Insights, Trends, Outlook and Opportunity Analysis 2017-
2025.
Coherent Market Insights (2017): Agricultural Biological Market, by Product, by Source, by Mode of
Application, by Application, and by Geography - Global Trends and Forecast to 2025.
https://www.coherentmarketinsights.com/market-insight/agricultural-biological-market-1029
Foundational Paper by the International Sustainable Chemistry Collaboration Centre for the GCO II
51 May 2018
Daniell, W. E. ; Van Tung, L. ; Wallace, Ryan M. et al. (2015): Childhood Lead Exposure from Battery
Recycling in Vietnam. BioMed Research International, 2015 (193715).
DeGusta, M. (2012): Are Smart Phones Spreading Faster than Any Technology in Human History?
MIT Technology Review, https://www.technologyreview.com/s/427787/are-smart-phones-spreading-
faster-than-any-technology-in-human-history/, accessed 9 May 2018.
Deloitte (2010): The Chemical Multiverse - Preparing for Quantum Changes in the Global Chemical
Industry.
Deloitte (2018): Making the Future of Mobility: Chemicals and Specialty Materials in Electric,
Autonomous, and Shared Vehicles.
Deloitte;VCI (2017): Chemistry 4.0: Growth through Innovation in a Transforming World.
EEA (2014): Assessment of Global Megatrends – an update. Global megatrend 9: Increasingly severe
consequences of climate change. Copenhagen: European Environment Agency.
EEA (2015): The European Environment: State and Outlook 2015: Assessment of Global Megatrends.
Copenhagen: European Environment Agency.
EIA (2018): Annual Energy Outlook 2018, with Projections to 2050. Washington, DC: US Energy
Information Administration.
Ellen MacArthur Foundation (2017a): A New Textiles Economy: Redesigning Fashion's Future.
Ellen MacArthur Foundation (2017b): The New Plastic Economy: Rethinking the Future of Plastics.
ExxonMobil (2017): Outlook for Energy: A View to 2040.
EY (2017a): The Upside of Disruption: Megatrends Shaping 2016 and Beyond.
EY (2017b), Chemicals Trends Analyser..
FAO (2017a): The Future of Food and Agriculture – Trends and Challenges. Rome: Food and
Agriculture Organization of the United Nations.FAO (2017b): World fertilizer trends and outlook to
2020. Rome: Food and Agriculture Organization of the United Nations.
Fashion for Good; Safer Made (2018): Safer Chemistry Innovation in the Textile and Apparel Industry.
Favarò, F. M.; Nader, N.; Eurich, S. O.; Tripp, M.; Varadaraju, N. (2017): Examining Accident Reports
Involving Autonomous Vehicles in California. PLOS One, 12(9), e0184952.
Forschungszentrum Juelich (2017): Renaissance of the Iron-Air Battery: Charging and Discharging
Reactions during Operation shown with Nanometer Precision." ScienceDaily..
https://www.sciencedaily.com/releases/2017/11/171116105004.htm, accessed 10 May 2018.
Frost & Sullivan (2014): World’s Top Global Mega Trends To 2025 and Implications to Business,
Society and Cultures.
Gaines, L. (2014): The Future of Automotive Lithium-Ion Battery Recycling: Charting a Sustainable
Course. Sustainable Materials and Technologies 1–2; 2–7.
Global Construction Perspectives;Oxford Economics (2015): Global Construction 2030: A Global
Forecast for the Construction Industry to 2030. London.
Global Fashion Agenda;Boston Consulting Group (2017): Pulse of the Fashion Industry.
Global Market Insights (2017): Construction Chemicals Market Size - Industry Share Report 2024.
Green, D. (2016): The World’s top 100 Economies: 31 countries; 69 Corporations.
https://blogs.worldbank.org/publicsphere/world-s-top-100-economies-31-countries-69-corporations
accessed 12 May 2018.
Foundational Paper by the International Sustainable Chemistry Collaboration Centre for the GCO II
52 May 2018
Haefliger, P.; Mathieu-Nolf, M.; Lociciro, S. et al. (2009): Mass Lead Intoxication from Informal Used
Lead-Acid Battery Recycling in Dakar, Senegal. Environmental Health Perspectives, 117(10): 1535–
1540.
Høibye, L.; Sand, H. (2018): Circular Economy in the Nordic Construction Sector. Copenhagen: Nordic
Council of Ministers.
Huang, L.; Krigsvoll, G.; Johansen, F.; Liua, Y.; Zhang, X. (2018): Carbon Emission of Global
Construction Sector. Renewable and Sustainable Energy Reviews, 81(2), 1906-1916
Hurst, C. (2010): China’s Rare Earth Element Industry. What can the West Learn? Washington, DC:
Washington Institute for the Analysis of Global Security.
Intertek (N/A): URL: http://www.intertek.com/beauty-products/testing/cosmetotextile/ accessed 10 May
2018.
IEA (2016): Energy Efficiency: Market Report 2016. Paris: International Energy Agency.
IEA (2017): Energy Technology Perspectives 2017: Catalysing Energy Technology Transformations.
Paris: International Energy Agency.
IEA; WBCSD (2018): Technology Roadmap - Low-Carbon Transition in the Cement Industry.
Paris: International Energy Agency; Geneva: World Business Council for Sustainable Development.
Heffer, P., Prud’homme, M. (2016): Global Nitrogen Fertiliser Demand and Supply: Trend, Current
Level and Outlook. Paper and Presentation at the 7th International Nitrogen Initiative Conference, 4-8
December 2016, Melbourne, Australia.
IMO (2015): Third IMO Greenhouse Gas Study 2014. London: International Maritime Organization.IFC
(2007): General, Environmental, Health, and Safety Guidelines. Washington, DC: International
Finance Corporation.
IHS Market (2016): Textile Chemicals- Speciality Chemicals Update Program.
URL: https://ihsmarkit.com/products/chemical-textile-scup.html, accessed 10 May 2018.
ILO (2016): ASEAN in transformation. Textiles, Clothing and Footwear: Refashioning the Future.
Geneva: International Labour Organization.
International Lead Association (2012): Lead Uses – Statistics. https://www.ila-lead.org/lead-facts/lead-
uses--statistics, accessed 10 May 2018.
IRENA (2018): Renewable Energy and Jobs. Annual Review 2018. Masdar City: International
Renewable Energy Agency.
Jaakkola, J.K.; Knight, T. L. (2008): The Role of Exposure to Phthalates from Polyvinyl Chloride
Products in the Development of Asthma and Allergies: A Systematic Review and Meta-analysis.
Environmental Health Perspectives, 116(7), 845-853.
Jones, N. (2013): A Scarcity of Rare Material is Hindering Green Technologies. Yale Environment 360:
https://e360.yale.edu/features/a_scarcity_of_rare_metals_is_hindering_green_technologies, accessed
10 May 2018.
Julander, A.; Lundgren, L.; Skare, L. et al. (2014): Formal Recycling of E-Waste leads to Increased
Exposure to Toxic Metals: An Occupational Exposure Study from Sweden. Environment International,
73, 243-251.
Kanchongkittiphon, W.; Mendell, M. J.; Gaffin, J. M.; Wang, G.; Phipatanakul, W. (2015): Indoor
Environmental Exposures and Exacerbation of Asthma: An Update to the 2000 Review by the Institute
of Medicine. Environmental Health Perspective, 123(1), 6-20.
Kant, R. (2012): Textile Dyeing Industry and EnvironmentalHhazard. Natural Science, 4:1, 22-26..
Foundational Paper by the International Sustainable Chemistry Collaboration Centre for the GCO II
53 May 2018
KEMI (2016): Hazardous Chemicals in Construction Products – Proposal for a Swedish Regulation.
Stockholm: Swedish Chemicals Agency.
KEMI (2014): Chemicals in Textiles - Risk to Human Life and the Environment. Swedish Chemicals
Agency.
KPMG (2016): Future State 2030: The Global Megatrends Shaping Governments.
Kümmerer, K (2017): Sustainable Chemistry: A Future Guiding Principle. Angewandte Chemie
International Edition, 56, 2–4.
Kummerer, K.; Dionysiou, D.D., Olsson, O; Fatta-Kassinos, D. (2018): A Path to Clean Water.
Science, 361 (6399), 222-224.
Kuijp, T. J. van der; Huang, L.; Cherry, C. R. (2013): Health Hazards of China’s Lead-acid Battery
Industry: A Review of its Market Drivers, Production Processes, and Health Impacts. Environmental
Health, 12:61.
Landrigan, P. J.; Fuller, R.; Acosta, N. J. R. et al. (2018): The Lancet Commission on Pollution and
Health. The Lancet, 391, 10119, 462–512.
Larcher, D.; Tarascon, J.-M. (2015): Towards Greener and More Sustainable Batteries for Electrical
Energy Storage. Nature Chemistry, 7, 19-29.
Lauster, G., Mildner S.-A., Richter S. (eds.) (2011): Resource Scarcity – A Global Security Threat?
Berlin: Stiftung Wissenschaft und Politik.
Lemmens, C.; Luebkemann, C. (2016): The Circular Economy in the Built Environment. London: Arup.
Lim, S.-R.; Kang, D.; Ogunseitan, O. A.; Schoenung, J. E. (2011): Potential Environmental Impacts of
Light-Emitting Diodes (LEDs): Metallic Resources, Toxicity, and Hazardous Waste Classification.
Environmental Science & Technology, 45(1), 320-327.
Liu, Y., Sun Q., Li W., Adair KR., Li J., Sun X. (2017): A Comprehensive Review on Recent Progress in
Aluminum–Air Batteries. Green Energy & Environment 2 (3), 246-277.
Lundgren, Karin (2012): The Global Impact of E-Waste: Addressing the Challenge. Geneva:
International Labour Organization.
Lv, W.; Wang, Z.Cao, H. et al. (2018): A Critical Review and Analysis on the Recycling of Spent
Lithium-Ion Batteries. ACS Sustainable Chemistry & Engineering, 6 (2), 1504-1521.
Maddalena, R.; Roberts, J. J.; Hamilton, A. (2018): Can Portland Cement be replaced by Low-Carbon
Alternative Materials? A Study on the Thermal Properties and Carbon Emissions of Innovative
Cements. Journal of Cleaner Production, 186, 933-942.
Matthews, J. T. (1997): Power Shift. Foreign Affairs, 76(1), 50-66.
Minter, A. (2018): China's Giving Batteries a Second Life. Bloomberg:
https://www.bloomberg.com/view/articles/2018-03-11/china-s-giving-batteries-a-second-life, accessed
10 May 2018.
Moseson, A. J. ; Moseson, D.E. ; Barsoum, M.W. (2012): High Volume Limestone Alkali-Activated
Cement Developed by Design of Experiment. Cement and Concrete Composites, 34 (3), 328-336.
National Intelligence Council (2017): Global Trends: Paradox of Progress. Washington, DC.
Nazari, A.; Sanjayan, J. G. (eds.) (2017): Handbook of Low Carbon Concrete. London/Cambridge:
Elsevier.
Nimpuno, N.; Scruggs, C. (2011): Information on Chemicals in Electronic Products. Copenhagen:
Nordic Council of Ministers.
Foundational Paper by the International Sustainable Chemistry Collaboration Centre for the GCO II
54 May 2018
OECD (2012): Environmental Outlook to 2050: The Consequences of Inaction. Paris: OECD
Publishing.
OECD (2016a): Science, Technology and Innovation Outlook 2016. Paris: OECD Publishing.
OECD (2016b): The Economic Consequences of Outdoor Air Pollution. Paris: OECD Publishing.
OECD (2018): Economic Outlook for Southeast Asia, China and India 2018 - Fostering Growth
through Digitalisation. Paris: OECD Publishing.
OECD; IEA (2014): Africa Energy Outlook: A Focus on Energy Prospects in Sub-Saharan Africa.
Paris: International Energy Agency.
OECD; IEA (2017): World Energy Outlook 2017. Paris: International Energy Agency.
Ohajinwa, C. M.; Van Bodegom, P. M.; Vijver, M. G.; Peijnenburg, W. J. G. M. (2017): Health Risks
Awareness of Electronic Waste Workers in the Informal Sector in Nigeria. Int J Environ Res Public
Health. 14(8): 911.
Perkowski, J. (2017): EV Batteries: A $240 Billion Industry In The Making That China Wants To Take
Charge Of. https://www.forbes.com/sites/jackperkowski/2017/08/03/ev-batteries-a-240-billion-industry-
in-the-making/#30a5f7f93f08, accessed 10 May 2018.
Persistence Market Research (2016): Global Market Study on Consumer Electronics.
Philp, J., 2018, The Bioeconomy, the Challenge of the Century for Policy Makers. New Biotechnology,
40 (A), 11-19.
Plastics Europe (2012): Plastics: Architects of Modern and Sustainable Buildings. Brussels: Plastics
Europe.
Pool, R. (2012): Releasing the Rare Earths. Engineering & Technology, 7, 72-75.
Pucher, J.; Buehler, R. (2017): Cycling Towards a More Sustainable Transport Future. Transport
Reviews, 37:6, 689-694.
Pure Earth; Green Cross Switzerland (2016): World’s Worst Pollution Problems 2016: The Toxics
Beneath our Feet. New York; Zurich.
PwC (2015): Glimpsing the Future(s): Transformation in the Chemicals Industry.
PwC (2017a): The Long View: How Will the Global Economic Order Change by 2050?
PwC (2017b): Chemicals Industry Trends, Delivering profitable growth in a hypercompetitive, low-
growth world.
PwC (2018): Five Trends Transforming the Automotive Industry.
QuintilesIMS Institute (2016): Outlook for Global Medicines through 2021: Balancing Cost and Value.
Research and Markets (2017): Growth Opportunities in the Global Construction Industry.
Retief, F.; Bond, A.; Pope, J.; Morrison-Saunders, A.; King, N. (2016): Global Megatrends and their
Implications for Environmental Assessment Practice. Environmental Impact Assessment Review, 61,
52–60.
Rodrigue, J.P. (2017): The Geography of Transport Systems. Fourth Edition. New York: Routledge.
Roland Berger (2015): Chemicals 2035 – Gearing up for Growth.
Roland Berger (2016): Digitization in the Construction Industry: Building Europe's Road to
"Construction 4.0".
Foundational Paper by the International Sustainable Chemistry Collaboration Centre for the GCO II
55 May 2018
Roland Berger (2017): Trend Compendium 2030. Megatrend 4 Climate Change and Economic Risk
https://www.rolandberger.com/en/Dossiers/Trend-Compendium.html, accessed 10 May 2018.
Ruijven, B. J. van; Vuuren, D. P. van; Boskaljon, W. et al. (2016): Long-term Model-based Projections
of Energy Use and CO2 Emissions from the Global Steel and Cement Industries. Resources,
Conservation and Recycling, 112, , 15-36.
Satterthwaite, D.; McGranahan, G.; Tacoli, C. (2010): Urbanization and Its Implications for Food and
Farming. Philosophical Transactions of the Royal Society B; 365(1554): 2809–2820.
Swanson, A. (2015): How China used More Cement in 3 years than the U.S. did in the Entire 20th
Century. https://www.washingtonpost.com/news/wonk/wp/2015/03/24/how-china-used-more-cement-
in-3-years-than-the-u-s-did-in-the-entire-20th-century, accessed 9 May 2018.
Scruggs, C. E.; Nimpuno, N.; Moore, R. B.B. (2016): Improving Information Flow on Chemicals in
Electronic Products and E-waste to Minimize Negative Consequences for Health and the Environment.
Resources, Conservation and Recycling, 113, 149-164.
Stanway, D. (2017): China's Recyclers Eye Looming Electric Vehicle Battery Mountain. Reuters:
https://www.reuters.com/article/us-china-batteries-recycling-insight/chinas-recyclers-eye-looming-
electric-vehicle-battery-mountain-idUSKBN1CR0Y8, accessed 10 May 2018.
Technavio Research (2017): Key Findings of the Global Eco Fiber Market.
https://www.businesswire.com/news/home/20180415005117/en/Key-Findings-Global-Eco-Fiber-
Market-Technavio, accessed 10 May 2018.
The Ecologist (2016): Dirty Business: Africa's Unregulated Lead Battery
Smelting, https://theecologist.org/2016/mar/03/dirty-business-africas-unregulated-lead-battery-
smelting, accessed 10 May 2018.
Thienen, G. van; Spee, T. (2008): Health Effects of Construction Materials and Construction Products.
Tijdschrift voor toegepaste Arbowetenschap, 2008(1).
Transparency Market Research (2018): Textile Chemicals Market - Global Industry Analysis, Size,
Share, Growth, Trends, and Forecast, 2018–2026.
Tür, M.; Manhart, A.; Schleicher, T. (2016): Generation of Used Lead-acid Batteries in Africa –
Estimating the Volumes. Freiburg: Öko-Institut.
UNDESA (2014a): World Urbanization Prospects: The 2014 Revision. United Nations, Department of
Economic and Social Affairs, Population Division (ST/ESA/SER.A/366).
UNDESA (2014b): World Urbanization Prospects: The 2014 Revision, Highlights. United Nations,
Department of Economic and Social Affairs, Population Division (ST/ESA/SER.A/352).
UNDESA (2014c): Cities for a Sustainable
Future. http://www.un.org/en/development/desa/news/ecosoc/cities-for-a-sustainable-
future.html, accessed 10 May 2018.
UNDESA (2017): World Population Prospects: The 2017 Revision, Key Findings and Advance Tables.
Working Paper No. ESA/P/WP/248. United Nations, Department of Economic and Social Affairs,
Population Division.
UNDESA (2018): World Urbanization Prospects: The 2018 Revision - Key Facts. United Nations,
Department of Economic and Social Affairs, Population Division
UNDP; UNRISD (2017): Global Trends: Challenges and Opportunities in the Implementation of the
Sustainable Development Goals. New York; Geneva: United Nations Development Programme;
United Nations Research Institute for Social Development.
Foundational Paper by the International Sustainable Chemistry Collaboration Centre for the GCO II
56 May 2018
UN Environment (2018a): The Weight of Cities: Resource Requirements of Future Urbanization.
Report by the International Resource Panel. Nairobi: United Nations Environment Programme.
UN Environment (2018b): Analysis of Best Practices in Sustainable Chemistry. SAICM/IP.2/INF.9,
http://www.saicm.org/Portals/12/documents/meetings/IP2/IP_2_INF_9_Analysis_Best_Practices_Sust
_Chem.pdf, accessed 10 May 2018.
UN Environment (2017): CCAC High Level Assembly endorses Global Strategy on Low-sulfur Fuels and
Cleaner Diesel Vehicles https://www.unenvironment.org/news-and-stories/blog-post/ccac-high-level-
assembly-endorses-global-strategy-low-sulfur-fuels-and
UNEP (2013a): Global Chemicals Outlook - Towards Sound Management of Chemicals. Geneva:
United Nations Environment Programme.
UNEP (2013b): Costs of Inaction on the Sound Management of Chemicals. Geneva: United Nations
Environment Programme.
UNGA (2017): Fulfilling the Promise of Globalization: Advancing Sustainable Development in an
Interconnected World. Report of the Secretary-General. A/72/301. New York: United Nations General
Assembly.
UNHABITAT (2016): World Cities Report 2016: Urbanization and Development: Emerging Futures.
Nairobi: United Nations Human Settlements Programme..
UNIDO (2015): Industrial Development Report 2016: The Role of Technology and Innovation in
Inclusive and Sustainable Industrial Development. Vienna: United Nations Industrial Development
Organization..
Valencia, R. C. (2013): The Future of the Chemical Industry by 2050. Zurich: Wiley-VCH.
Vandyke, N.; Englert, D. (2017): Three Reasons Why Maritime Transport Must Act on Climate
Change. Blog: Transport for development; the World Bank Group.
http://blogs.worldbank.org/transport/three-reasons-why-maritime-transport-must-act-climate-change,
accessed 10 May 2018.
VCI (2013): Zukunft der Energiespeicher. Chemie-Report 11:2013. Frankfurt am Main.
VCI (2016): Chemiewirtschaft wichtiger Länder, https://www.vci.de/die-branche/zahlen-
berichte/chemiewirtschaft-wichtiger-laender-laenderberichte-und-laenderkurzberichte.jsp accessed 10
May 2018.
VCI (2018): Eckdaten der chemisch-
pharmazeutischen Industrie zu Forschung, Entwicklung und Bildung.
VCI (2013): Factbook 06: „Chemie 2030 - Globalisierung gestalten".
VCI (2017): The German Chemical Industry 2030: VCI-Prognos Study – Update 2015/2016.
Weiss, T. G.; Seyle, D. C.; Coolidge, K. (2013): The Rise of Non-State Actors in Global Governance:
Opportunities and Limitations. One Earth Future Foundation.
Wexler, P. (2012): Chemicals, Environment, Health - A Global Management Perspective. Baton
Rouge: CRC Press.
WHO (2018): Ambient (Outdoor) Air Quality and Health. http://www.who.int/news-room/fact-
sheets/detail/ambient-(outdoor)-air-quality-and-health, accessed 10 May 2018.
WHO (2016): Ambient Air Pollution: A Global Assessment of Exposure and Burden of Disease.
Geneva: World Health Organization.
WIPO (2016): World Intellectual Property Indicators 2016. Geneva: World Intellectual Property
Organization.
Foundational Paper by the International Sustainable Chemistry Collaboration Centre for the GCO II
57 May 2018
WIPO (2017): World Intellectual Property Indicators 2017. Geneva: World Intellectual Property
Organization.
World Bank (2017): Transport., http://www.worldbank.org/en/topic/transport/overview. Accessed: 6
May 2018.
World Bank (2018): Global Economic Prospects: Broad-Based Upturn, but for How Long? Washington
DC, World Bank Group.
World Economic Forum (2017): Shaping the Future of Construction: Insights to Redesign the Industry.
White Paper.
World Economic Forum (2015): Deep Shift: Technology Tipping Points and Societal Impact.
ZVEI (2017): The Global Electrical & Electronic Industry – Facts & Figures. German Electrical and
Electronic Manufacturers’ Association.
Foundational Paper by the International Sustainable Chemistry Collaboration Centre for the GCO II
58 May 2018
6. Annex I: Lists of Megatrends in Selected Studies
UNDP and UNRISD (2017): Global Trends: Challenges and Opportunities in the Implementation
of the Sustainable Development Goals
1. Poverty and inequalities
2. Demography
3. Environmental degradation and climate change
4. Shocks and crises
5. The changing context of development cooperation and financing sustainable
development
6. Domestic and international private business and finance
7. Technological innovations for Sustainable Development
UNGA (2017): Fulfilling the promise of globalization: advancing sustainable development in an
interconnected world. Report of the Secretary-General
1. Shift in production and labour markets
2. Rapid advances in technology
3. Climate change
National Intelligence Council (2017): Global Trends: Paradox of Progress
1. The rich are aging, the poor are not
2. The global economy is shifting
3. Technology is accelerating progress but causing discontinuities
4. Ideas and Identities are driving a wave of exclusion
5. Governing is getting harder
6. The nature of conflict is changing
7. Climate change, environment, and health issues will demand attention
KPMG (2016): Future State 2030: The global megatrends shaping governments
Foundational Paper by the International Sustainable Chemistry Collaboration Centre for the GCO II
59 May 2018
1. Demographics
2. Rise of the individual
3. Enabling technology
4. Economic interconnectedness
5. Public debt
6. Economic power shift
7. Climate change
8. Resource stress
9. Urbanization
EEA (2015): The European Environment: State and Outlook 2015: Assessment of Global
Megatrends.
1. Diverging global population trends
2. Towards a more urban world
3. Changing disease burdens and risks of pandemics
4. Accelerating technological change
5. Continued economic growth?
6. An increasingly multipolar world
7. Intensified global competition for resources
8. Growing pressures on ecosystems
9. Increasingly severe consequences of climate change
10. Increasing environmental pollution
11. Diversifying approaches to governance
EY (2017): The upside of disruption: Megatrends shaping 2016 and beyond
1. Industry redefined
2. The future of smart
3. The future of work
4. Behavioral revolution
5. Empowered customer
6. Urban world
7. Health reimagined
8. Resourceful planet
Frost and Sullivan (2014): World’s Top Global Mega Trends to 2025 and Implications to
Business, Society, and Cultures (2014 Edition)
Foundational Paper by the International Sustainable Chemistry Collaboration Centre for the GCO II
60 May 2018
1. Connectivity and convergence
2. Bricks and clicks
3. Smart is the new Green
4. Future of energy
5. Future of mobility
6. Infrastructure development
7. Economic trends
8. Urbanization
9. Social trends
10. Health, wellness, and wellbeing
11. Innovating to zero
12. New business models
OECD (2016): OECD Science, Technology and Innovation Outlook 2016.
1. Demography
2. Natural resources and energy
3. Climate change and environment
4. Globalisation
5. Role of governments
6. Economy, jobs and productivity
7. Society
8. Health, inequality and well-being
World Economic Forum (2015): Deep Shift: Technology Tipping Points and Societal Impact
1. People and the internet
2. Computing, communications and storage everywhere
3. The Internet of Things
4. Artificial intelligence (AI) and big data
5. The sharing economy and distributed trust
6. The digitization of matter
VCI (2017): The German Chemical Industry 2030: VCI-Prognos Study – Update 2015/2016
Foundational Paper by the International Sustainable Chemistry Collaboration Centre for the GCO II
61 May 2018
1. Growing and ageing world population
2. Globalisation is losing in speed
3. Faster dissemination of technologies and knowledge
4. No shortage of energy and raw materials to 2030
5. Environmental and climate protection are gaining in importance worldwide
6. Public debt impairs growth
Valencia (2013): The Future of the Chemical Industry by 2050.
1. Social
• Population
• Demographics
• Urbanization
2. Economic
• World economic growth
• BRIC economic
• Foreign direct investment
3. Political
• New international order
• Corporate economies
• Social networks
• A people’s world
4. Energy
• Oil, gas, others
5. Climate change
6. Wild cards
Deloitte (2010): The chemical multiverse: Preparing for quantum changes in the global
chemical industry
1. Demographic change
2. Quality health care
3. New patterns of mobility
4. Convergence of technologies
5. Globalization
6. New patterns of consumption
7. Resource scarcity (energy, water, and food)
8. Climate change/green
9. Urbanization