Outcomes
In brief, the students learned that the measured DBHs were significantly different for rain trees (mean ± stdev = 99 ± 22 cm; range = 56–154 cm) compared with the other trees in the plot (10 ± 4 cm; 4–19 cm). The corresponding mean heights were also significantly different: 16 ± 3 m (10–21 m) versus 6 ± 2 m (2–12 m). Total AGCB and BGCB estimates for the plot were 53 and 10 Mg C, respectively. Of the total carbon biomass (63 Mg C; equivalent to 231 Mg CO2eq), nearly all (62 Mg; 231 Mg CO2eq) was associated with the 23 mature rain trees (assuming they are 40 years old). The mean carbon content of each rain tree was 2.7 ± 1.4 Mg C (9.9 ± 0.2 Mg CO2eq), which corresponds to a carbon sequestration rate of 67 kg C/year (245 kg CO2eq/year), which is on the high side for tropical trees reported in the literature. All differences in DBH, height, and biomass were significantly different at α = 0.05 (unpaired t-test on log-transformed values).
Given the freedom to explore the real-world implications of the tree-planting initiative, the students created a wide variety of dissemination “products” in the spirit of a newsworthy piece written in layperson language for the public. Some of the most informative narratives placed the carbon sequestration gains in the context of student’s own carbon footprint, vehicle emissions in their city-nation of Singapore, Singapore’s carbon footprint, and/or loss of carbon via tropical forest removal (so-called deforestation). Estimates of the carbon lost from tropical deforestation are widespread in a variety of online media and academic/science papers (e.g., Pearson et al. 2017). One student couched the article in terms of the carbon imprint of a family’s vacation (Carbon Footprint Ltd. 2020); another in terms of transportation back and forth from school annually.
Again, students were not told how to derive their extended findings, forcing them to use research skills when necessary. However, unlike even a few years ago, there are many online sources to help make these estimates. For example, online carbon footprint calculators, such as those of The Nature Conservancy (2020) are easy to use and provide reasonable estimates. Other online tools allows one to estimate emissions from buildings, car trips, and public transport (e.g., Google Environmental Insights Explorer 2020; International Civil Aviation Organization, The United Nations 2020).
The following passage, which combines findings reported by a few students, demonstrates the learning/contextualization process. The global mean carbon footprint is 5 Mg CO2/year per person, which is about one-half of the equivalent mass in one rain tree (again 9.9 ± 0.2 Mg CO2eq). In developed countries, the mean footprint is higher and varies (World Bank 2014): e.g., ~ 10 Mg CO2 in Singapore; 16.5 Mg CO2 in the USA. Interestingly, the Singapore footprint is roughly that of one mature rain tree. Thus, the CO2 equivalent mass of the 23 rain trees in the green space (231 Mg CO2eq) accounts for the carbon footprint of approximately 23 years of one’s life in Singapore. However, most trees are much smaller than rain trees. If an equivalent mass of 2 Mg CO2eq is assumed for the average tree, a Singaporean student would need to plant five trees (and leave to maturation) each year to offset their annual carbon footprint. More than 420 trees would then be needed to account for their lifetime footprint (mean life expectancy is 84 years). A student traveling from Singapore to Los Angeles for a vacation would need to plant two trees to offset the CO2 emissions from taking this flight (~ 3.9 Mg CO2 emissions). Two and a half trees are roughly equivalent to driving a car 18,000 km in a year (Government Technology Agency of Singapore 2020).
Many students concluded that climate change mitigation by tree planting alone was, therefore, limited in terms of practicality and scale. The 5.6 million Singaporean residents would need to plant about 28 million “average” trees per year, which is about 40,000 trees per km2, to offset the carbon footprint of the national population. To offset the country’s estimated 40 million Mg of annual CO2 emissions, 20 million new trees would need to be planted each year. In recognizing the impractical nature of such a massive (re)planting, students became aware of the limitation of this solution as a climate change strategy—regardless of the scientific issues. Many then chose to highlight “other” benefits of tree planting, such as increased aesthetics, biodiversity preservation, cooling effects to offset the urban heat island effect, and the potential to trap pollutants. In the end, most students were drawn to paying more close attention to their personal carbon footprints and promoting alternative energy solutions—a result that is inline with both our objective of the exercise, and the goals of sustainability teaching (see “Promoting sustainability education”).
Critical discussions
Here, we point out that the science regarding the true benefit of tree (re)planting on the removal of atmospheric CO2 is debated and still evolving (Green et al. 2019). Nevertheless, the comparisons above helped the students frame a complicated science issue in understandable terms given their various backgrounds. Further, it was the students who made the analogies, not us. Nevertheless, these framings opened the door to further discussions, for example about the trade-offs/feedbacks of planting in different geographical locations (tropics versus temperate/boreal regions); current availability of “deforested” lands (i.e., some are urbanized; others under agriculture); differences between tree-based landscapes and other ecosystems including grasslands; how much of the carbon produced during photosynthesis is transferred to other stores, especially the soil; water use and nutrient demand of trees; the time frame for carbon sequestration; and the fact that tree-planting is not the same as whole ecosystem restoration.
With respect to fieldwork, common observations included reference to: (a) disturbance of rain trees by pruning that creates great biomass variation; (b) difficulty of measuring tree height on uneven ground and for wide canopies that obscured the view of the top of the tree; (c) measurement differences between team members; (d) vastly different canopy shapes for trees of similar height (related to a); and (e) a wide variety of tree species of different forms within the “other tree” category for which a common allometric equation was used to estimate biomass. These are common issues flagged by researchers performing similar fieldwork. Thus, the major concerns of the students regarding their calculations revolved around two issues (cf. Vorster et al. 2020): (1) measurement error in the field; and (2) appropriateness of the carbon biomass allometric equations.
With regard to measurement error and uncertainty, many students were concerned about the estimation of H. Tree height measurements are fraught with error because of the difficulty of seeing the location of the top of the tree (Phalla et al. 2018). Thus, there is large uncertainty in the angle from which H is determined. Further, the measurement is complicated if the ground is not level, which was the case because some of the site was on sloping ground. For some tall trees, estimates from all group members varied by as much as 2 to 4 m. Large errors in H (up to 25% for example) produced uncertainties in the biomass estimate that were equivalent to smaller errors in the D term, which is squared in Eq. 1. Fortunately, the measurement error for D is small, on the order of a few mm. Concerned with the H term, students, therefore, considered other approaches such as using sophisticated technologies (e.g., LiDAR), triangulation from the top of a building, and using an allometric equation that does not rely on tree height (cf. Phalla et al. 2018).
Concerns were voiced regarding the appropriateness of the two allometric equations (Eqs. 3 and 4) for calculating biomass in the plot. Students questioned their applicability initially because they were developed for tropical trees in general, not for the trees in the plots, specifically (cf. Hunter et al. 2013). For example, one student commented that “When estimating for carbon biomass of urban trees, there tend[s] to be an overestimation–especially if we take streetscapes into account–due to regular pruning”. The student was questioning the accuracy of the estimation from a general allometric relationship that did not account for canopy changes from routine maintenance. However, as Singapore-specific equations do not exist, pantropical equations or ones from similar locales must be used (Yuen et al. 2013). They were also concerned because the determined biomass values were very high compared with other trees in the tropics, including Singapore (Ngo and Lum 2018).
Following these reflections, we introduced the following alternative allometric equations as alternatives to Eqs. 3 and 4, respectively:
$${\text{AGB } = \text{ exp}}\left[ { - {1}.{8}0{3 }{-} \, 0.{\text{976 E }} + \, 0.{\text{976 ln}}\left( p \right) \, + { 2}.{\text{673 ln}}\left( {\text{D}} \right) \, {-} \, 0.0{299 }} \right[{\text{ln}}\left( {\text{D}} \right)\left] {^{{2}} } \right]$$
(5)
$$BGB = 0.023 * D^{2.59}$$
(6)
where Eq. 5 (Chave et al. 2014) does not use height as a variable; and Eq. 6 was determined from individual root systems in a primary dipterocarp forest in Pasoh Forest Reserve, Peninsular Malaysia (Niiyama et al. 2010). Further, Eq. 5 includes the term E that refers to the “health” of the tree stand; it represents factors such as stress from drought, (mis)management, disease, and land degradation.
Incorporation of the two additional equations allowed for other types of analysis:
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1.
Given a value of E (normally assigned a value of 0.5) in Eq. 5, compare the AGCB values computed by Eqs. 3 and 5;
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2.
Compare the BGCB values determined from Eqs. 4 and 6;
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3.
Assuming an accurate and known plot-level AGCB, determine a new value of E such that Eq. 5 produces a similar value;
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4.
Perform a sensitivity analysis for all equations to determine how much estimates vary for subtle changes of each input variable (D, H, p).
These advanced equations allow students to use various packages to explore the data graphically and perform basic statistical tests such as the paired t-test (parametric assumption) or the Wilcoxon ranked sign test (nonparametric assumption). The inclusion of Eq. 5, provided an opportunity for students to implement the advanced Excel Solver function, which is an add-in program that allows one to determine an optimal value by changing variables within one or more equations (e.g., changing E such that the AGB values from Eqs. 3 and 5 have the lowest cumulative/mean difference for all trees). Important in this process is allowing students of all levels to experiment beyond their current repertoire of skills, without being penalized for not being strong in math or computer science.
Informal assessment
At the end of the semester, we surveyed two separate groups of students using a modified version of the questionnaire of Schroeder et al. (2006). The volunteer online survey questions were emailed to 38 students enrolled in the Test module; 32, in the Control. We present it here as though it was a formal assessment, but in reality, it was an exercise for us to judge effectiveness to guide future teaching. Nevertheless, we present the outcome here because it demonstrates the positive outcome of the collaborative approach.
The demographics of the students in the two modules are practically the same in that they were almost equally split in gender and all were Singaporean nationals who were pursuing degrees related to geography or environmental sciences. Few had a strong background in STEM subjects. Given the homogeneity and small size, other demographics were not considered to be important influencing variables in our assessment that was focused on exposure to content. We simply asked the students if “Trees are an effective means of storing carbon”. Students were then asked to indicate the extent to which they agreed or disagreed with the following statements regarding the ecosystem services of urban trees:
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1.
Contributes to your sense of well-being
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2.
Cools the surrounding environment
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3.
Improves aesthetics
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4.
Improves hydrological functioning of the environment
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5.
Filters aerosols/pollutants from the air
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6.
Increases wildlife habitats
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7.
Mitigates climate change by storing carbon
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8.
Provides shade
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9.
Reduces noise pollution
Their responses were recorded on a six-point scale, with possible responses ranging from 1 (Strongly disagree) to 6 (Strongly agree). Our main interest was on the responses to statement 7 regarding the role of trees to store carbon and offset the impacts of greenhouse gas (namely CO2) emissions to the atmosphere. While the other statements do relate to ecosystem services provided by urban trees, the student views on their role were largely irrelevant to our assessment, but again, provide insight on student exposure to environmental issues. The responses were ranked accordingly to how strongly the students agreed with the statements regarding the role of trees. The critical difference between the two classes was that storing carbon ranked high (3rd) with the Test class, but low (8th) with the Control class who did not do the exercise. We attribute this major difference to the exposure of carbon accounting that the Test class received during the carbon exercise described herein. While we do not claim the results to be a rigorous evaluation, to a certain extent, they were useful to us in evaluating the usefulness of the exercise as an effective mode of conveying information. The ordering of many of the other statements was not surprising, giving the emphasis of urban heat island phenomena, sense of place and natural capital in other modules commonly taken by the students in Singapore.