Published at : 09 Dec 2021
Volume : IJtech
Vol 12, No 5 (2021)
DOI : https://doi.org/10.14716/ijtech.v12i5.5252
Harri Pyykkö | VTT Technical Research Centre of Finland Ltd., FI-02044 Espoo, Finland |
Ville Hinkka | VTT Technical Research Centre of Finland Ltd., FI-02044 Espoo, Finland |
Tuomo Uotila | LUT University, FI-15210 Lahti, Finland |
Rosa Palmgren | VTT Technical Research Centre of Finland Ltd., FI-02044 Espoo, Finland |
Seaports
(hereafter “ports”) within the European Union are facing increasingly
restrictive regulation in the near future from various sources driven by
climate change prevention and public opinion supporting “green” values. Ports
are complex hubs for maritime transportation systems and global supply chains,
as well as an integral part of critical national infrastructures. However, they
are also significant individual sources of harmful emissions, and their
involvement is crucial to reducing transportation-related environmental
impacts. To meet future regulatory requirements, stakeholders will need to find
ways to align their policies accordingly and create long-term pathways toward
these ambitious targets. The empirical case study presented in this paper among
European Port Cluster (EPC) stakeholders distinctly reflects the mounting
importance of environmental policies and the need for further preparative
measures for meeting future demands. This paper emphasizes the intensified
impact of forthcoming regulation on existing business models in the EPC and
contributes a foresight-based framework to approaching this issue
systematically. The adoption of future-oriented regulation is a non-linear,
potentially disruptive, and complex foresight process that requires each
stakeholder to formulate their own strategic pathway toward a target-seeking
scenario. Changing direction from the status quo toward sustainability also
requires a strong commitment beyond mere regulatory compliance.
Backcasting; Emissions; Port; Regulation; Sustainability
Seaborne transportation is
a vitally important part of global trade, and within the European Union (EU)
region, there are up to 1,200 active seaports (hereafter
“ports”; ENISA, 2019). As ports handle more
than 80% of global trade, they are also considered a critical national
infrastructure (UNCTAD, 2018). However,
globally, significant amounts of harmful emissions caused by port operations, as
well as by vessels, trucks, and trains visiting the ports, create air pollution
and jeopardize the well-being of nearby inhabitants. In addition, greenhouse
gas (GHG) emissions are accelerating climate change (UNEP,
2021). An extensive sustainability survey of 36 ports in North America,
Europe, and the Asia-Pacific (Hossain et al., 2021)
concluded that European ports are slightly ahead in terms of
sustainability progress, but that there is an urgent need for rapid improvement
in adopting actions that address climate change.
Climate change and related environmental challenges have been identified as the most essential megatrends that predominantly affect the future development of all freight transportation systems (Maraš et al., 2019). There is already extensive empirical research data available (e.g., Oeder et al., 2015) that demonstrate how harmful fossil fuels are to public health and the environment when used within the port infrastructure (PI).
The
business-as-usual approach in the European Port Cluster (EPC) is evidently not
a sufficient pathway (Laffineur, 2012), and
a growing body of scholars (e.g., Bjerkan and
Seter, 2019; Berawi, 2021) are highlighting the requirement for diverse
research and new initiatives to support actions toward sustainability.
Operational activities within the PI have traditionally been considered very energy-intensive
(Pavlic et al., 2014). Moreover, improved
energy efficiency is considered a vital effort toward the mitigation of port
emissions, which requires large-scale investments in
new and more state-of-the-art equipment (Ganda,
2019), as well as the utilization of alternative energy sources (Pavlic et al., 2014). Table 1 summarizes the
complexity of governing emission sources with respect to multiple different
stakeholders operating within the PI and coastal areas. Each stakeholder has a
certain influence on the overall emissions occurring within the PI, and their
combined emission mitigation efforts define the overall results (Lai et al., 2013).
Although regulation is recognized as a strong driver of sustainability
transition (ST), there are also major hindrances, such as organizational path
dependencies (e.g., Teece et al., 1997) and
various lock-in effects (Markard et al., 2012),
resulting primarily from the high capital intensity distinctive of transport
systems (Bernardino et al., 2015). Table 1
shows how regulation related to ports developed between 2013 and 2021 in the
EU. In 2021, the EU set a target of making the continent carbon-neutral by 2050
and cutting CO2 emissions by 55% by 2030 compared with the levels in
1990. However, the trend leading to this decision was already visible in other
regulations since 2013. In theory, this extensive timeframe allowed actors to
adjust their existing business models to meet the upcoming regulatory
requirements of carbon neutrality several years before the actual decision was
made in 2021. However, the research literature (e.g.,
Banerjee, 2001) proposes that due to the complexity of the topic,
regulation often does not have direct causal impacts and can result in
inadvertent outcomes despite the original purpose (Soria-Lara
and Banister, 2018).
Table 1 Regulatory framework applicable within the port cluster in the EU
Regulatory Initiative |
Year |
Reference |
As a part of its “Ports: an engine for growth” report, the European
Commission suggested that ports become more active in improving the
environmental image of waterborne transport by implementing an infrastructure-charging
system that favors vessels fulfilling predefined environmental standards. |
2013 |
European Commission, 2013 |
According to the circular economy approach, waste can be turned into
a resource by reusing, repairing, refurbishing, and recycling existing
materials and products. |
2014 |
European Commission, 2014 |
European Commission has invited the member states and the European
maritime industry to work together toward the long-term objective of “zero
waste, zero emissions” in maritime transport. |
2016 |
European Commission, 2016 |
The EU strives to minimize its dependence on oil and to mitigate the
environmental impacts of transport. |
2017 |
European Commission, 2017 |
EU and its member states to become a carbon-neutral region by 2050,
including a target of 55% minimum reduction in GHG emissions by 2030. |
2020 |
European Commission, 2020 |
The European Green Deal regulatory framework has been approved. The program’s objective is for
the continent to become carbon-neutral by 2050. |
2021 |
European Commission, 2021 |
ST toward more sustainable port operations is a
complex, potentially disruptive, and long-term process that requires new
policies and innovative solutions (Pavlic et al., 2014), in addition to the ability
of each involved stakeholder to plan ahead (Schrettle
et al., 2014). However, there is evidence (e.g.,
Becker and Caldwell, 2015) that some notable decisions regarding
sustainability within the port domain are still driven by short-term economic
benefits rather than focusing on long-term planning toward sustainability and
the future requirements of port operations. Hence, the use of foresight methods
to formulate future scenarios has been recognized as a workable conceptual tool
to systematically approach this issue (Berawi,
2016; Yashin et al., 2020). Foresight activities can also be utilized to
provide decision-makers with information about different scenarios and to potentially
visualize how passive approaches are in conflict with predominant insights about
the future (McDonald et al., 2018). The
objective of this paper is two-fold: (1) to analyze empirical survey results
and research literature findings in order to reflect the findings against the
upcoming regulatory framework; and (2) to review, align, and contextualize the
most suitable foresight method in order to formulate a process framework model
that would develop long-term sustainability-related regulatory adoption in the
EPC.
Based
on the empirical survey and research literature findings, it is evident that
the organizations within EPC need to accelerate their sustainability efforts in
order to meet the upcoming regulatory framework. Due to the complexity and
non-linear mechanisms involved, ambitious emission reduction goals can be
achieved in a sustainable way only with long-term strategic planning and a
proactive approach. This paper presented a contextualized backcasting-based
foresight framework using a target-seeking approach as a novel conceptual
contribution to tackle this complex issue. This paper further suggests that
once EPC stakeholders implement sustainability governance-related tools similar
to FRAP as a rigid part of their future strategies, they will support the generation
of ST roadmaps and improve the identification of potential investment needs and
major obstacles in advance.
The
authors wish to acknowledge the “COREALIS” project, which has received funding
from the European Union’s Horizon 2020 research and innovation programme under
grant agreement No. 768994. The content reflects solely the authors’ view, and
the EU is not responsible for any use of the information it contains.
McDonald, K.S., Hobday, A.J., Fulton, E.A.,
Thompson, P.A., 2018. Interdisciplinary Knowledge Exchange Across Scales in a Globally
Changing Marine Environment. Global Change Biology, Volume 24(7), pp. 3039–3054
McDonald, K.S., Hobday, A.J., Thompson,
P.A., Lenton, A., Stephenson, R.L., Mapstone, B.D., Dutra, L.X.C., Bessey, C.,
Boschetti, F., Cvitanovic, C., Bulman, C.M., Fulton, E.A., Moeseneder, C.H.,
Pethybridge, H., Plagányi, E.E., Ingrid van Putten, E., Rothlisberg, P.C.,
2019. Proactive, Reactive, and Inactive Pathways for Scientists in a Changing World.
Earth's Future, Volume 7(2), pp. 60–73
Min, H., Galle, W., 2001. Green Purchasing Practices
of US Firms. International Journal of Operations & Production Management,
Volume 21(9), pp. 1222–1238
Nonaka, I., 1994. A Dynamic Theory of
Organizational Knowledge Creation. Organization
Science, Volume 5(1), pp. 14–37
Oeder, S., Kanashova, T., Sippula, O.,
Sapcariu, S.C., Streibel, T., Arteaga-Salas, J.M., Passig, J., Dilger, M.,
Paur, H-R., Schlager, C., Mülhopt, S., Diabaté, S., Stengel, B., Rabe, R., Harndorf, H., Torvela, T., Jokiniemi, J.K., Hirvonen,
M-R., Schmidt-Weber, C., Traidl-Hoffmann, C., BéruBé, K.A., Wlodarczyk, A.J., Prytherch,
Z., Michalke, B., Krebs, T., Prévôt, A.S.H., Kelbg, M., Tiggesbäumker, J., Karg,
E., Jakobi, G., Scholtes, S., Schnelle-Kreis, J., Lintelmann, J., Matuschek,
G., Sklorz, M., Klingbeil, S., Orasche, J., Richthammer, P., Müller, L., Elsasser,
M., Reda, A., Gröger, T., Weggler, B., Schwemer, T., Czech, H., Rüger, C.P., Abbaszade,
G., Radischat, C., Hiller, K., Buters, J.T.M., Dittmar, G., Zimmermann, R., 2015.
Particulate Matter from Both Heavy Fuel Oil and Diesel Fuel Shipping Emissions
Show Strong Biological Effects on Human Lung Cells at Realistic and Comparable
In Vitro Exposure Conditions, PLoS One, Volume 10(6), pp. 1–17
Pavlic, B., Cepak, F., Sucic, B., Peckaj,
M., Kandus, B., 2014. Sustainable Port Infrastructure, Practical Implementation
of the Green Port Concept AU. Thermal Science, Volume 18(3), pp. 935–948
Quist, J., 2007. Backcasting for a
Sustainable Future: The Impact After 10 Years. Eburon Academic Publishers,
Delft, Netherlands
Robinson, J., 1990. Futures Under Glass: A Recipe
for People Who Hate to Predict. Futures Volume 22(8), pp. 820–842
Robinson, J., Burch, S., Talwar, S.,
O’Shea, M., Walsh, M., 2011, Envisioning Sustainability: Recent Progress in the
use of Participatory Backcasting Approaches for Sustainability Research. Technological
Forecasting & Social Change, Volume 78(5), pp. 756–768
Schreier, M., 2014. Qualitative Content
Analysis. Sage Handbook of Qualitative Data Analysis. SAGE Publications
ltd
Schrettle, S., Hinz, A., Scherrer-Rathje,
M., Friedli, T., 2014. Turning Sustainability into Action: Explaining Firms'
Sustainability Efforts and Their Impact on Firm Performance. International
Journal of Production Economics, Volume 147(Part A), pp. 73–84
Soria-Lara, J.A., Banister, D., 2018.
Evaluating the Impacts of Transport Backcasting Scenarios with Multi-Criteria
Analysis. Transportation Research Part A: Policy and Practice, Volume
110, pp. 26–37
Soria-Lara, J.A., Banister, D., 2018.
Collaborative Backcasting for Transport Policy Scenario Building. Futures, Volume
95, pp. 11–21
Sotarauta, M., Kautonen, M., Lähteenmäki, T.,
2002. Tulevaisuustiedosta kilpailuetua: Teknologian Ennakointikonsepti. SENTE-publication
14/2002. University of Tampere
Storper, M., 1997. The Regional World,
Territorial Development in a Global Economy. Guilford Press/NY
Swart R.J., Raskin, P., Robinson, J., 2004.
The Problem of the Future: Sustainability Science and Scenario Analysis. Global
Environmental Change, Volume 14(2), pp. 137–146
Tay, M.Y., Rahman, A.A., Aziz, Y.A., Sidek,
S., 2015. A Review on Drivers and Barriers towards Sustainable Supply Chain
Practices. International Journal of Social Science and Humanity, Volume
5(10), pp. 892–897
Teece, D., Pisano, G., Shuen, A., 1997.
Dynamic Capabilities and Strategic Management. Strategic Management Journal,
Volume 18(7), pp. 509–533
Teece, D., Pisano, G., 1994. The Dynamic
Capabilities of Firms: An Introduction. Industrial and Corporate Change,
Volume 3(3), pp. 537–556
Teece, D.J., 2000. Strategies for Managing
Knowledge Assets: The Role of Firm Structure and Industrial Context. Long Range Planning, Volume 33(1), pp.
35–54
UNCTAD, 2018. Review of Maritime Transport.
UNCTAD/RMT/2018. Available Online at https://unctad.org/system/files/official-document/rmt2018_en.pdf,
Accessed on August 22, 2021
UNEP, 2021. United Nations Environmental
Program. Why Does Global Clean Ports Matter. Available Online at https://www.unep.org/explore-topics/transport/what-we-do/global-clean-ports/why-does-global-clean-ports-matter,
Accessed on August 25, 2021
Vergragt, P.J., Quist, J., 2011. Backcasting
for Sustainability: Introduction to the Special Issue. Technological Forecasting
& Social Change, Elsevier Inc, New York
Wiek, A., Iwaniec, D., 2014. Quality Criteria
for Visions and Visioning in Sustainability Science. Sustainability Science,
Volume 9, pp. 497–512
Yashin, S., Yashina, N., Koshelev, E.,
Kashina, O., Pronchatova-Rubtsova, N., 2020. Foresight of Volga Federal
District Innovation System Development using a Multi-Objective Genetic
Algorithm. International Journal of Technology, Volume 11(6),
pp. 1171–1180
Zahra, S., George, G., 2002. Absorptive Capacity: A
Review, Reconceptualization, and Extension. The Academy of Management Review,
Volume 27(2), pp. 185–203