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Article

Offsetting the Impact of CO2 Emissions Resulting from the Transport of Maiêutica’s Academic Campus Community

by
Guilherme Veludo
1,
Manuel Cunha
1,
Maria Manuel Sá
1,2,3,* and
Carla Oliveira-Silva
1
1
UNICES, Research Unit in Management and Sustainability, Business and Science Department, University of Maia, 4475-690 Maia, Portugal
2
CICGE, Geo-Space Sciences Research Centre, 4169-002 Porto, Portugal
3
CISA, Research Centre for Health and Environment, 4200-072 Porto, Portugal
*
Author to whom correspondence should be addressed.
Sustainability 2021, 13(18), 10227; https://doi.org/10.3390/su131810227
Submission received: 14 August 2021 / Revised: 7 September 2021 / Accepted: 9 September 2021 / Published: 13 September 2021

Abstract

:
The authors aim to investigate the number of trees necessary to capture the CO2 emissions from house–campus travelling, to and from the Maiêutica Academic Campus in the north of Portugal. A sample of the academic community was given an online survey in order to assess mobility practices. Based on the data collected, CO2 emissions, as well as the number of trees necessary to mitigate these emissions, were calculated. The authors estimate that the total emissions resulting from house–campus commutes amount to 2937 tCO2 year−1. To mitigate this amount of carbon dioxide, 138 ha would be necessary to plant 96,539 trees, according to the species’ respective CO2 removal rates. The estimated tree area necessary to neutralize the community’s mobility related CO2 emissions is so high that other alternatives must be considered: a preferred use of public transportation, carpool system, online theoretical classes, rescheduling timetables, green roofs installation, and photovoltaic panels.

1. Introduction

1.1. The Emissions of CO2 from Transports

The Earth is a planet with finite resources. Even though there is a decreasing tendency in the use of fossil fuels, increasing the preference for renewable energy sources, fossil fuels still represent 71% of the gross energy available in the European Union (EU) [1]. In Portugal, the transport sector still has one of the highest energy consumption rates (37.2%) of the total primary energy among other activity sectors [2]. This sector makes one of the most significant contributions to the increase of greenhouse gases, GHG (CO2, CH4, N2O, HFCs, PFCs, SF6, and NF3). According to the European Environment Agency [3], transport accounts for 27% of the total CO2 European emissions to the atmosphere. GHGs, due to anthropogenic emissions, are responsible for climate changes, in particular the temperature increase in the last 30 years [4]. To achieve the objectives set by the Paris Agreement, and keep the global average temperature increase well below 2 °C, the European Union (EU) defined performance requirements for new passenger cars. Firstly, Regulation (EC) No 443/2009 was published, setting the emission limit at 130 gCO2/km and 95 gCO2/km, for 2015 and 2020, respectively [5]; and more recently, with Regulation (EU) 2019/631, the bar of 95 gCO2/km for 2020 was confirmed, and reductions for the following years were planned [6]. In 2020, the European Commission [7] put forward a goal to reduce 1990 values of greenhouse gases by a minimum of 55% by 2030. The escalation of the policies is due to the long period of time that key areas, like the transport sector, take to readjust, as the Commission pointed out. If these goals are not successfully implemented by 2030, the necessary adaptations to fulfil 2050 goals would have to happen at an unrealistically high speed. According to this document, “the transport sector had the lowest share of renewable energy in 2015, with only 6%. By 2030, this has to increase to around 24% through further development and deployment of electric vehicles, advanced biofuels and other renewable and low carbon fuels as part of a holistic and integrated approach”.

1.2. The Capture of CO2 from the Atmosphere

According to the literature, the capture of CO2 can be made with technology or with biomass [8]. Technology requires direct air capture and uses physical and chemical processes. As an example, CO2 can be injected in geological strata, like old cold mines, oil wells, and saline aquifers [9,10,11,12]. However, this alternative comprises high costs and leakage risks [13].
Biomass resorts to the biological process of photosynthesis, a natural process of carbon capture by the trees, to remove CO2 from the atmosphere [8,14,15,16,17], the alternative championed by the Kyoto Protocol [18].
Recently, some authors have studied different biomes or forest ecosystems’ (tundra, rain forest, woodlots, etc.) capacity to capture carbon from the atmosphere [17,19], defining the carbon footprint parameter known as Average Forest Carbon Sequestration (AFCS). Other authors have been looking into specific trees’ capacity to capture CO2 [15,16]. Their method depends on the measurement of the trees’ diameter and height. From that data, the tree’s weight is estimated and multiplied by the factors 0.725, 0.50, and 3.6663 to estimate the tree’s dry weight organic matter, amount of carbon, and CO2 sequestered, respectively; finally, by dividing the result by the tree’s, age, we get the annual amount of captured CO2. Nevertheless, information regarding the annual amount of carbon dioxide removed by different tree species is still scarce.

1.3. Universities’ Role in Keeping Sustainable Practices

There has been an increasing focus on many organizations’ and institutions’ sustainable development and environmental management. According to Ferrer-Balas et al. [20], it was the 5th Environmental Management for Sustainable Universities (EMSU) International Conference, held in Barcelona, Spain in October of 2008, that led universities to rethink how they were dealing with the matter of sustainability.
In June 2012, in Rio de Janeiro, Brazil, on the occasion of the United Nations Conference on Sustainable Development, chancellors, presidents, rectors, deans, and leaders of higher education institutions and related organizations all signed the “Commitment to Sustainable Practices of Higher Education Institutions” pledging to a series of actions, among which was to green the campuses by reducing the environmental footprint, encouraging more sustainable lifestyles [21].
Universities in Europe, such as the Norwegian University of Technology and Science [22], the Technical University of Madrid [23], or the University of Castilla La-Mancha [24] are pursuing the goals of sustainability, estimating carbon footprints, and making inventories of carbon emissions. In Britain, there is a Higher Education Carbon Management (HECM) program aimed at helping universities to set up a carbon management plan, forecasting and targeting carbon emissions and sequestration [15]. However, most of these works, when they mention transportation-related carbon footprint normally refer to the service industry, as is the case with Larsen et al. [22], Alvarez et al. [23], and Gómez et al. [24] from the Norwegian University of Technology and Science, the University of Madrid, and the University of Castilla-La Mancha, respectively.
Gibassier et al. [25] consider the climate vulnerability and the future carbon accounting a social issue; because of that, as faculty members and university students alike are part of the most educated sector of the population on matters of sustainability practices, they should be the ones to educate the remaining population and contribute to climate change prevention.
Portugal, in the Ministers’ Cabinet Resolution n° 53/2020 [26], reaffirmed its commitment to achieving carbon neutrality by 2050, proposing to reduce its greenhouse gas (GHG) emissions by 85% to 90% relative to 2005 values. Among the many greenhouse gas emission reduction sectorial goals is a 40% reduction in the transport sector’s emissions.

1.4. Maiêutica Academic Campus

Maiêutica is a higher education cooperative in the city of Maia, near Oporto, in the north of Portugal. The academic campus of Maiêutica started to be built in February 1995 on the cooperative grounds, and since then it has undergone several expansions, currently occupying 7 ha. Currently, there are two institutions on campus, the University of Maia and the Polytechnic Institute of Maia. Together, they serve a population of 4378 individuals: 4000 (91.4%) students, 313 (7.1%) professors and research staff, and 65 (1.5%) administrative and service staff. The academic community mainly comes from the metropolitan area of Porto (75%), while 20% come from frontier districts and just 5% from the rest of the country.

1.5. Goals

This is one of the few studies carried out on CO2 emissions resulting solely from the academic community’s commute. As was mentioned, some universities’ or higher education schools’ carbon footprint papers can be found in the literature, but there is very little information regarding academic communities’ transport-related emissions.
In this paper, the authors aim to calculate the academic community’s carbon emissions, as it concerns house–campus travelling (round trip), to and from the Maiêutica Academic Campus; determine the number of trees necessary to capture the CO2 emissions resulting from those travels; inform the community about their contributions to their mobility-related carbon footprint; offer suggestions for more sustainable mobility strategies; and contribute to achieving the target set by the Portuguese government of reducing transport-related emissions, increasing awareness to this problem.

2. Methods

2.1. Samples and Procedures

An online survey was designed to collect data about transportation to and from the campus. The survey was specifically developed for this investigation and pre-tested before application. The questionnaire had thirteen questions, twelve of which were closed: number of trips done to campus per week, use of car, distance done by car (round trip in km), mean number of car occupants, fuel type, car age, usage of metro, distance done by metro (round trip in km), use of train, distance done by train (round trip in km), use of bus, and distance done by bus (round trip in km). Additionally, there was an open question regarding the use of other means of transportation. The target population of this study consisted of a community of 4378 individuals working or studying at the Academic Campus of Maiêutica. Data collection was conducted in April 2019, and during this period, two emails were sent to the community calling for answers to the survey.
The link to the questionnaire was sent to all institutional emails, and the answers allowed the distribution of the respondents’ profile according to professor (or researcher), student, or administrative (or service) staff. Data treatment was developed using IBM SPSS Statistics software, version 25, International Business Machines Corporation, New Orchard Road, Armonk, New York 10504, USA.

2.2. Estimation of Carbon Emissions

Because some of the respondents commute on their way to campus and back, the weekly carbon emission was determined by adding the various to and from mobility-related emissions of every participant, according to the following equations
C E w e e k = N × i = 1 n ( d i y i × E i ) .  
D =   d i y i
where:
  • C E w e e k —carbon emission per week (g CO2) per respondent,
  • N—number of trips done to campus per week,
  • d i —partial distance in a given transportation i (km)
  • y i —number of occupants in a given car ( y i = 1 for other transports),
  • E i —transport i’s average carbon emission (g CO2/km), and
  • D—campus–home and home–campus total distance for each participant (km)
Cars’ carbon emissions were based on the values on Table 1. Account was taken of the type of fuel and the age of the vehicle. In instances of car sharing, CO2 emission was divided by the number of passengers as shown in Equation (1).
For collective means of transportation (subway, train, and bus), the carbon emission estimate was based on Table 2 and, in this case, values corresponded to individual passengers.

2.3. Estimation of Trees Needed to Capture CO2

The Portuguese Forest Management Regional Program [34] identifies, for every Portuguese region and sub-region, the forest species that should be protected, in accordance with their high economic, heritage, and cultural value, their relationship with the region’s history and culture, their scarcity, and their role in habitat support. The maritime pine (Pinus pinaster), the eucalyptus (Eucalyptus globulus), the Portuguese oak (Quercus faginea), the Pyrenean oak (Quercus pyrenaica), the holm oak (Quercus rotundifolia), and the cork oak (Quercus suber) are among the species whose protection should be prioritized in the region of the Maiêutica Academic Campus.
Considering the mild, dry climate of the region, and taking into account the data presented by Bernal et al. [17], reporting a 95% confidence interval, the removal rate, in tCO2 · ha−1 · year−1, for the above mentioned species are: pine 7.6 ± 2.0; eucalyptus 37.9 ± 5.5; and oak 5.3 ± 3.5. In order to determine the area necessary for planting these trees, a mean tree density of 700 stems per hectare was assumed, as observed by Crowther et al. [35] for a Mediterranean forest.

3. Results

3.1. Sample

A total of 490 individuals answered the survey: 174 professors and researchers (56% of the total teaching staff), 254 students (6% of the total student community), and 62 administrative and service staff (95% of the group). Figure 1 shows the distribution of transportation used on a round home–campus trip. Only 7.8% of the respondents make the trip by foot or bike (Others).
Only taking into account vehicle drivers and passengers, choice distribution for this trip by group, professors and researcher staff, students, and administrative and service staff, is shown on Table 3. As can be observed, the car is the preferred type of vehicle used by all three campus community groups, while students resort to public transportation the most.
Table 4 shows the 95% confidence interval for the distance travelled by each academic community group in a round house–campus trip for each type of vehicle.
Furthermore, we can see that the majority of cars (87.3%) hold only a single passenger, the driver him/herself. From those who resort to a car for transportation, only 4.2% of the professors group, 22.5% of students, and 11.3% of administrative and service staff surveyed carpool. Moreover, 79.1% of carpool rides carry only 2 passengers.
Looking at fuel usage, we can see that 68.5% are diesel-fuelled, 29.1% are gasoline-fuelled, 1.6% are LPG, and only 0.8% run on no fuel (electric).
Table 5 shows the participants’ average car age, indicating that the professors and researchers staff group drives the newest cars, while students drive the oldest, over 10 years old.

3.2. CO2 Emission Estimate

The amount of CO2 emitted for the transportation of all three groups pertaining to the Maiêutica Academic Campus was determined as described in the methodology section, taking all factors into account. In order to estimate the annual carbon emissions (CEy), the statistics for campus attendance in the last five years were consulted. Registered data allowed us to conclude that the professors, students, and administrative staff groups travel 37, 32, and 48 weeks per year, respectively.
Thus, we calculated the sample’s carbon emission for the whole year of 2019 (Table 6). Dividing each group’s CO2 emissions by the group’s respective size in the sample (n), we get the individual’s average CO2 emission. The teachers group exhibited the highest average of CO2 emissions by individual (2.66 ton/year), while the students were the lowest individual emitters (0.51 ton/year).
Assuming that each group maintained the same pattern, that is, the same number of trips per week and choice of transportation, we calculated the CO2 emissions of the whole Maiêutica academic community released to the atmosphere. Globally, campus community travel account for 2937 t CO2 being emitted every year.

3.3. Number of Trees Needed to Capture CO2

As mentioned in the methodology section, the most common and indigenous trees in the Portuguese territory are the pine, the eucalyptus, and the oak. Taking into account the values observed by Bernal et al. [17] for the CO2 removal rate of each of these species, the required area, in hectares, to capture all of the CO2 emitted by the campus community’s annual travels is presented in Table 7. Assuming the value of 2937 tons CO2 year−1, and a single species planted, the total area required could vary between 77 hectares and 554 hectares. Considering that the tree density for a Mediterranean forest as stated by Crowther et al. [35] is of 700 stems per hectare, the number of trees necessary for each species varies from 53,900 to almost 387,800.
Given that these three native species might appear simultaneously in the same forest, according to the official percentages of each species provided by the Portuguese Institute of Nature and Forest Conservation [36], the number of necessary trees and respective area was determined, assuming they were all simultaneously present (Table 8).
Thus, close to 138 hectares would be necessary to plant the three tree species so as to compensate for the campus community’s travel emissions.
Despite the reforestation support funds made available by the 2020 Portuguese Regional Development Plan, the acquisition of such extensive plots of land and the planting of all the trees necessary to compensate for campus community travelling is not economically viable for any educational institution.
Results show that campus reforestation is impracticable and cannot be the only CO2 mitigating policy; thus, other initiatives must be in order.

4. Discussion

Even though there are papers concerning universities’ CO2 emissions, as is the case with the KIWI University of New Zealand [15], the School of Forestry Engineering Technical University of Madrid [23], and the University of Castilla-La Mancha [24], the CO2 values assessed generally include energy, waste, procurement, and travel; and in some cases, “travel” includes not only academic community’s mobility but also all the travelling implicated in the purchase and delivery of services and equipment, hindering an estimation comprising solely house–campus travelling (round trip) emissions. Larsen et al. [22] is an example of a study presenting an estimate for the Norwegian University of Technology and Science’s carbon footprint as it regards to students and employees’ travelling. This university, with seven faculties, has a total of 20,000 students and 5500 employers, reporting 16% of their general tCO2 emissions from 2009 resulting directly from such travelling. Thus, an estimate can be made pointing at 2.7 tCO2 year−1 per employee and 0.74 tCO2 year−1 per student. These values are similar to those established for the Maiêutica Academic Campus: 2.6 tCO2 year−1 per person for professors and research staff; 0.51 tCO2 year−1 per person for students; and 1.13 tCO2 year−1 per person for administrative and service staff.
The “my car” culture is still too strong; it is necessary that we abandon the idea of the car as a symbol of consumption and status and start thinking about mobility as a social and environmental question. The results are clear regarding the percentage of CO2 emissions, and other GHGs, due to the community’s favourite medium of transportation, the car. Our sample’s average number of passengers per car, 1.2 passengers/car, is lower than the Environment Portuguese Agency asserts, 1.6 passenger/car [2]. By looking at Table 6, we can see that a teacher emits five times more CO2 than a student due to the choices he/she makes regarding his/her type of transportation.
For the good of the future, a change in mentality is imperative, namely in choosing a collective means of transportation or other less polluting alternatives. In the last two decades, we have witnessed the rise of new ways to use one’s car, aiming mainly at reducing traffic, parking problems, and environmental abuse: car sharing and carpooling. Car sharing, a similar concept to time sharing for housing, has even more economic advantages, with less buying, maintenance, and insurance expenses than environmental ones. Carpooling is a more environmentally attractive concept. This system uses a private or company car to drive more than one passenger, later rotating the cars between the participants. The benefits are evident: reducing fuel and maintenance expenses, reducing the number of cars in circulation, reducing travelling time with less traffic, decreasing stress and tiredness, and alleviating parking problems and, as a consequence, very significantly, pollution. In fact, a study conducted in a service company in Italy showed that a reduction of CO2 through a carpooling system could vary between 22% and 28% [37]. Recently, another study in the coastal area of Espinho (Portugal) estimated that carpooling could lead to a reduction in carbon emissions of between 25% and 30% [38]. There are, today, international projects focused on this carpooling system (www.compartir.org, accessed on 28 April 2021). A similar app, managed by the Students Association and/or the Maiêutica Administration, promoting connections between people taking the same route, might gather more supporters.
Looking at the results showing how many hectares and trees are necessary, it is not economically viable to neutralize community-related emissions of CO2 solely by resorting to a tree planting strategy. Concurrently, green roofs could be installed atop the campus buildings, planting mainly herbaceous plants and small bushes, thus allowing thermal isolation of the building and CO2 capture.
Another option would be the assembly of photovoltaic panels, whose renewable energy production would counter-balance the emission of CO2 associated with the community’s mobility.
Organizational policies like online theoretical classes and schedule replanning so as to reduce the necessity for round trips would be yet another option.
The need for a culture of sustainability integrated into educational and research programs has already been pointed out by some authors [23,39]. From an educational and academic point of view, the institution could develop a course, open to all degrees, where circular economy, the carbon footprint, and all the more pressing environmental questions of today could be approached, so as to appeal to the academic community and the surrounding civil society.
The present study did not consider such factors as driving behavior, vehicle configuration and traffic conditions, or side winds, rain, and road grade, which may have significant effects in fuel consumption in real-world driving [40].
It would be interesting in the future to inquire whether the installation of environmentally sustainable university housing, close to campus, would show a significant impact in carbon emission reduction.

5. Conclusions

The Maiêutica Academic Campus releases 2.937 tonnes of CO2 to the atmosphere, per year, due to community trips. Most of these emissions come from students as they represent the largest sector of the community (91.4%) even though, individually, they are the lowest emitters at 0.51 ton year−1 · individual−1.
To compensate the total CO2 emissions, native species such as pine, eucalyptus, or oak should be planted. However, according to our calculations, 270,200, 53,900, or 387,800 trees, respectively, would be necessary. These results are interesting because for eucalyptus, 77 ha is enough, which is significantly less than for pine, 386 ha, and extremely less than the 555 ha required for oak. For the planting of the three species simultaneously, using the proportions indicated by the Portuguese Institute of Nature and Forest Conservation, 138 hectares are needed, and, in total, 96,530 trees would need to be planted.
Facing the number of hectares and trees necessary for neutralizing the carbon dioxide emissions, it is clear that it is not viable to implement this as an isolated solution, for several reasons. As such, the authors suggest a broader range of solutions, namely: more frequent use of collective transportation; green roofs installation and photovoltaic panels; online theoretical classes and schedules’ replanning; and a new app for carpooling.
The value we obtained pertaining to the number of trees necessary to mitigate the community’s carbon dioxide emission shows us how far we are from solving the environmental problem the world is facing. The decision makers, the politicians, and the community in general should look at this work, reflect, and make decisions more in accordance with the preservation of the planet.

Author Contributions

The design and conduct of this research was equally shared between the authors. The four authors collaborated to produce this paper. C.O.-S. and M.C. proposed and developed the research design and methodology; M.M.S. and G.V. developed the manuscript writing and data analysis; C.O.-S. and M.C. supervised the work, provided additional comments on the results, and interpretation; and M.M.S. reviewed and approved the final version. All authors have read and agreed to the published version of the manuscript.

Funding

There was no funding for these research activities.

Institutional Review Board Statement

The study was carried out in accordance with the guidelines of the Declaration of Helsinki, with full respect for the Regulation of the Ethics and Deontology Committee of ISMAI of 29 June 2018.

Informed Consent Statement

Informed consent was obtained from all subjects involved in the study.

Data Availability Statement

The data presented in this study are available on request from the corresponding author. The data are not publicy available due to data which also forms part of an ongoig study.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. EUROSTAT. Share of Fossil Fuels in Gross Available Energy. Available online: https://ec.europa.eu/eurostat/web/products-eurostat-news/-/ddn-20210204-1 (accessed on 23 March 2021).
  2. State of the Environment Portal. Passenger Transport, Portugal. Available online: https://rea.apambiente.pt/content/passenger-transport?language=en (accessed on 23 March 2021).
  3. European Environment Agency. Annual European Union Greenhouse Gas Inventory 1990–2017 and Inventory Report 2019, Presented at the United Nations Framework Convention on Climate Change and the Kyoto Protocol 27 May 2019. Brussels. Available online: https://www.eea.europa.eu/publications/european-union-greenhouse-gas-inventory-2019 (accessed on 4 April 2021).
  4. Allen, M.R.; Dube, O.P.; Solecki, W.A.; Aragón-Durand, F.; Cramer, W.; Humphreys, S.; Kainuma, M.; Kala, J.; Mahowald, N.; Mulugetta, Y.; et al. Framing and Context. In Global Warming of 1.5 °C. An IPCC Special Report on the Impacts of Global Warming of 1.5 °C above Pre-Industrial Levels and Related Global Greenhouse Gas Emission Pathways, in the Context of Strengthening the Global Response to the Threat of Climate Change, Intergovernmental Panel on Climate Change; Masson-Delmotte, V., Zhai, P., Portner, H.-O., Roberts, D., Skea, J., Shukla, P.R., Pirani, A., Moufouma-Okia, W., Péan, C., Pidcock, R., et al., Eds.; IPCC: Geneva, Switzerland; Available online: https://www.ipcc.ch/site/assets/uploads/sites/2/2019/05/SR15_Chapter1_Low_Res.pdf (accessed on 20 March 2021).
  5. European Union. Regulation (EC) No 443/2009 of the European Parliament and of the Council of 23 April 2009 Setting Emission Performance Standards for New Passenger Cars as Part of the Community’s Integrated Approach To Reduce CO2 Emissions from Light-Duty Vehicles. Off. J. Eur. Union 2009, 140, 5–6. [Google Scholar]
  6. European Union. Regulation (EU) 2019/631 of the European Parliament and of the Council of 17 April 2019 setting CO2 Emission Performance Standards for New Passenger Cars and for New Light Commercial Vehicles, and Repealing Regulations (EC) No 443/2009 and (EU) No 510/201. Off. J. Eur. Union 2019, 151, 15. [Google Scholar]
  7. European Commission. Communication from the Commission to the European Parliament, the Council, the European Economic and Social Committee and the Committee of the Regions. Stepping up Europe’s 2030 Climate Ambition. Investing in a Climate-Neutral Future for the Benefit of Our People; European Commission: Brussels, Belgium, 2020. [Google Scholar]
  8. Lal, R. Carbon sequestration. Phil. Trans. R. Soc. B 2008, 363, 815–830. [Google Scholar] [CrossRef] [PubMed]
  9. Freund, P.; Ormerod, W.G. Progress towards storage of carbon dioxide. Energy Convers. Manag. 1997, 38, S199–S204. [Google Scholar] [CrossRef]
  10. Klara, S.M.; Srivastava, R.D.; McIlvried, H.G. Integrated collaborative technology development program for CO2 sequestration in geologic formations—United States Department of Energy R&D. Energy Convers. Manag. 2003, 44, 2699–2712. [Google Scholar]
  11. Rathnaweera, T.D.; Ranjith, P.G.; Perera, M.S.A. Experimental investigation of geochemical and mineralogical effects of CO2 sequestration on flow characteristics of reservoir rock in deep saline aquifers. Sci. Rep. 2016, 6, 1–12. [Google Scholar] [CrossRef] [Green Version]
  12. Li, Z.; Yuan, L.; Sun, G.; Lv, J.; Zhang, Y. Experimental determination of CO2 diffusion coefficient in a brine-saturated core simulating reservoir condition. Energies 2021, 14, 540. [Google Scholar] [CrossRef]
  13. Ranjan, M.; Herzog, H.J. Feasibility of air capture. Energy Procedia 2011, 4, 2869–2876. [Google Scholar] [CrossRef] [Green Version]
  14. IPCC. Land Use, Land Use Change and Forestry, Inter-Government Panel on Climate Change; Cambridge University Press: Cambridge, UK, 1999. [Google Scholar]
  15. De Villiers, C.; Chen, S.; Jin, C.; Zhu, Y. Carbon sequestered in the trees on a university campus: A case study. Sustainability Accounting. Manag. Policy J. 2014, 5, 149–171. [Google Scholar]
  16. Saral, A.M.; SteffySelcia, S.; Devi, K. Carbon storage and sequestration by trees in VIT University campus. In IOP Conference Series: Materials Science and Engineering; IOP Publishing: Bristol, UK, 2017; Volume 263, pp. 1–5. [Google Scholar]
  17. Bernal, B.; Murray, L.T.; Pearson, T.R.H. Global carbon dioxide removal rates from forest landscape restoration activities. Carbon Balance Manag. 2018, 13, 1–13. [Google Scholar] [CrossRef]
  18. Sedjo, R.A.; Marland, G. Inter-trading permanent emissions credits and rented temporary carbon emissions offsets: Some issues and alternatives. Clim. Policy 2003, 3, 435–444. [Google Scholar] [CrossRef]
  19. Mancini, M.S.; Galli, A.; Niccolucci, V.; Lin, D.; Bastianoni, S.V.; Wackernagel, M.; Marchettini, N. Ecological footprint: Refining the carbon footprint calculation. Ecol. Indic. 2016, 61, 390–403. [Google Scholar] [CrossRef]
  20. Ferrer-Balas, D.; Lozano, R.; Huisingh, D.; Buckland, H.; Ysern, P.; Zilahy, G. Going beyond the rhetoric: System-wide changes in universities for sustainable societies. J. Clean. Prod. 2010, 18, 607–610. [Google Scholar] [CrossRef]
  21. Commitment to Sustainable Practices of Higher Education Institutions on the Occasion of the United Nations Conference on Sustainable Development 20–22 June 2012, Rio de Janeiro Rio+20. Available online: https://sustainabledevelopment.un.org/content/documents/1889HEI%20Declaration%20English%20new%20version.pdf (accessed on 15 April 2021).
  22. Larsen, H.N.; Pettersen, J.; Solli, C.; Hertwich, E.G. Investigating the carbon footprint of a university—The case of NTNU. J. Clean. Prod. 2013, 48, 39–47. [Google Scholar] [CrossRef]
  23. Alvarez, S.; Blanquer, M.; Rubio, A. Carbon footprint using the compound method based on financial accounts. The case of the School of Forestry Engineering, Technical University of Madrid. J. Clean. Prod. 2014, 66, 224–232. [Google Scholar] [CrossRef]
  24. Gómez, N.; Cadarso, M.Á.; Monsalve, F. Carbon footprint of a university in a multiregional model: The case of the University of Castilla-La Mancha. J. Clean. Prod. 2016, 138, 119–130. [Google Scholar] [CrossRef]
  25. Gibassier, D.; Michelon, G.; Cartel, M. The future of carbon accounting research: “We’ve pissed mother nature off, big time”. Sustain. Account. Manag. Policy J. 2020, 11, 477–485. [Google Scholar] [CrossRef]
  26. Diário da República, n.° 133/2020. 1ª Série, de 10 de Julho. Resolução do Conselho de Ministros n° 53/2020. Available online: https://dre.pt/home/-/dre/137618093/details/maximized (accessed on 18 April 2021).
  27. The Carbon Trust. Energy and Carbon Conversions. The Carbon Trust: London, UK, 2008; Available online: http://www.carbontrust.co.uk/publications/publicationdetail.htm?productid=CTV033 (accessed on 7 April 2021).
  28. European Environment Agency. Monitoring CO2 Emissions from New Passenger Cars and Vans in 2015 EEA Report No 27/2016; Publications Office of the European Union: Luxembourg, 2017. [Google Scholar]
  29. Tsiakmakis, S.; Fontaras, G.; Ciuffo, B.; Samaras, Z. A simulation-based methodology for quantifying European passenger. Appl. Energy 2017, 199, 447–465. [Google Scholar] [CrossRef]
  30. Vilet, O.; Brouwer, A.S.; Kuramochi, T.; Broek, M.; Faaij, A. Energy use, cost and CO2 emissions of electric cars. J. Power Sources 2011, 196, 2298–2310. [Google Scholar]
  31. Metro do Porto. Sustainable Report 2018. Available online: https://www.metrodoporto.pt/uploads/document/file/486/RS2018.pdf (accessed on 22 April 2021).
  32. Trains of Portugal. Sustainable Report 2018. Available online: https://www.cp.pt/institucional/en/sustainable-management/sustainability-reports (accessed on 22 April 2021).
  33. Serviços de Transportes Coletivos do Porto. Sustainable Report 2011. Available online: https://www.stcp.pt/pt/institucional/sustentabilidade/relatorio-de-sustentabilidade/ (accessed on 26 April 2021).
  34. Portaria n.° 58/2019 de 11 de Fevereiro. Diário da República n° 29/2019–1.ª Série. Regulamento do Programa Regional de Ordenamento Florestal de entre Douro e Minho. Available online: https://dre.pt/home/-/dre/119386291/details/maximized (accessed on 28 April 2021).
  35. Crowther, T.W.; Glick, H.B.; Covey, K.R.; Bettigole, C.; Maynard, D.S.; Thomas, S.M.; Bradford, M.A. Mapping tree density at a global scale. Nature 2015, 525, 201–205. [Google Scholar] [CrossRef] [PubMed]
  36. ICNF—Institute for the Conservation of Nature and Forest. 6th National Forest Inventory: Main Results. Summary Report, v1.0. 2019. Available online: http://www2.icnf.pt/portal/florestas/ifn/ifn6 (accessed on 22 April 2021).
  37. Bruck, B.P.; Incerti, V.; Iori, M.; Vignoli, M. Minimizing CO2 emissions in a practical daily carpooling problem. Comput. Oper. Res. 2017, 81, 40–50. [Google Scholar] [CrossRef]
  38. Pinto, B.-M.; Rossetti, R.J.F. A Graph-Based Study of the Impact of Carpooling on CO2 Emissions. In Proceedings of the 2020 Forum on Integrated and Sustainable Transportation Systems (FISTS), Delft, The Netherlands, 3–5 November 2020. [Google Scholar]
  39. Stephens, J.C.; Graham, A.C. Toward an empirical research agenda for sustainability in higher education: Exploring the transition management framework. J. Clean. Prod. 2010, 18, 611–618. [Google Scholar] [CrossRef]
  40. Fontaras, G.; Nikiforos-Georgios, Z.; Biagio, C. Fuel consumption and CO2 emissions from passenger cars in Europe—Laboratory versus real-world emissions. Prog. Energy Combust. Sci. 2017, 60, 97–131. [Google Scholar] [CrossRef]
Figure 1. Distribution of transportation used on a round home–campus trip.
Figure 1. Distribution of transportation used on a round home–campus trip.
Sustainability 13 10227 g001
Table 1. Car emissions of CO2 by fossil fuel usage and age.
Table 1. Car emissions of CO2 by fossil fuel usage and age.
CarAverage Carbon
Emission (Ei)
(gCO2/km)
Source
Age > 10 years old
Gasoline 207[27,28]
Diesel197.9[27,28]
LPG164.7[28]
5 ≤ Age ≤ 10 years old
Gasoline 156.6[28]
Diesel151.2[28]
LPG137[28]
Vehicles < 5 years old
Gasoline 128.5[28,29]
Diesel126.9[28,29]
LPG98.3[28]
None (electric)52[30]
Table 2. Public transport emissions of CO2.
Table 2. Public transport emissions of CO2.
Public Transport Average Carbon Emission (Ei)
Per Passenger (gCO2/Km)
Source
Metropolitan 40[31]
Train 26.4[32]
Bus 82[33]
Table 3. Transports used in house–campus trip by each group from the Maiêutica Academic Campus community.
Table 3. Transports used in house–campus trip by each group from the Maiêutica Academic Campus community.
GroupPercentage of Group Individuals by Used Vehicle:
CarMetropolitanTrainBus
Prof Res. Staff94.4%5.1%00
Students52.8%34.6%5.6%7.0%
Adm. Ser. Staff85.5%14.5%0%0%
Table 4. Average distance travelled in a round trip and associated uncertainty (CI95) by type of transportation.
Table 4. Average distance travelled in a round trip and associated uncertainty (CI95) by type of transportation.
GroupDistance Travelled According to Transport (km/trip)
CarMetroTrainBus
MeanHalf CI95MeanHalf CI95MeanHalf CI95MeanHalf CI95
Teacher R. Staff46.111.214.49.7----
Students39.74.525.03.642.113.319.77.7
Adm. S. Staff30.76.037.113.8----
Table 5. Car age distribution among the three groups: professors and research staff, students, and administrative and service staff.
Table 5. Car age distribution among the three groups: professors and research staff, students, and administrative and service staff.
Car Age (Years)Prof. R. StaffStudentsAdm. S. Staff
age ≤ 5 40.7%23.8%28.3%
5 < age ≤ 10 32.3%25.2%39.6%
age > 10 26.9%51.0%32.1%
Table 6. Estimate of the annual CO2 emissions by the different groups and by individual.
Table 6. Estimate of the annual CO2 emissions by the different groups and by individual.
GroupSampleIndividualCommunity (Population)
nEmission
(tCO2 year−1)
Emission
(tCO2 year−1)
nEmission
(tCO2 year−1)
Emission
(%)
Prof. R. Staff1744632.6631383328.4
Students2541290.5140002.03169.1
Adm. S. Staff62701.1365732.5
Total490662 43782937
Table 7. Area and number of trees from a given species necessary to capture the annually emitted CO2 by the campus community’s travel.
Table 7. Area and number of trees from a given species necessary to capture the annually emitted CO2 by the campus community’s travel.
SpeciesRemoval Rate 1
(tCO2 year−1)
Required Area
(ha)
Number of Trees
Pine7.6386270,200
Eucalyptus37.97753,900
Oak5.3554387,800
1 Bernal et al. (2018).
Table 8. Number of trees and respective area occupied by the three species simultaneously.
Table 8. Number of trees and respective area occupied by the three species simultaneously.
Species% Coverage 2Required Area
(ha)
Number of Trees
Pine49.1%67.747,390
Eucalyptus45.6%62.944,030
Oak5.3%7.35110
Total 137.996,530
2 ICNF (2019).
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Veludo, G.; Cunha, M.; Sá, M.M.; Oliveira-Silva, C. Offsetting the Impact of CO2 Emissions Resulting from the Transport of Maiêutica’s Academic Campus Community. Sustainability 2021, 13, 10227. https://doi.org/10.3390/su131810227

AMA Style

Veludo G, Cunha M, Sá MM, Oliveira-Silva C. Offsetting the Impact of CO2 Emissions Resulting from the Transport of Maiêutica’s Academic Campus Community. Sustainability. 2021; 13(18):10227. https://doi.org/10.3390/su131810227

Chicago/Turabian Style

Veludo, Guilherme, Manuel Cunha, Maria Manuel Sá, and Carla Oliveira-Silva. 2021. "Offsetting the Impact of CO2 Emissions Resulting from the Transport of Maiêutica’s Academic Campus Community" Sustainability 13, no. 18: 10227. https://doi.org/10.3390/su131810227

APA Style

Veludo, G., Cunha, M., Sá, M. M., & Oliveira-Silva, C. (2021). Offsetting the Impact of CO2 Emissions Resulting from the Transport of Maiêutica’s Academic Campus Community. Sustainability, 13(18), 10227. https://doi.org/10.3390/su131810227

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