By Ren Junyao
Assignment 5 link: Please open the link, download and view.
In landscape architecture, data-integrated modeling of three-dimensional ecological performance is increasingly important. However, there is often a gap between the expected ecological benefits of vertical landscape designs and the actual outcomes observed in reality. Recognizing and understanding this discrepancy is a crucial first step for improving modeling accuracy and guiding future optimizations.
Does incorporating a vertical dimension in landscape design truly enhance biodiversity at the neighborhood scale? This project specifically asks whether existing vertical greenery installations are effectively improving local biodiversity.
The Wilmar Headquarters building at one-north was selected as the case study. This site features extensive vertical greenery, making it ideal for examining how 3D landscape design affects biodiversity.
Node Identification: Using the building’s landscape design plans, delineated every planted patch as a separate node. In practice, this means each green wall segment, rooftop garden, or ground-level planting area was marked out as an individual unit for analysis. These nodes form the basis of biodiversity assessment, as each is considered a distinct habitat area.
Habitat Value Scoring: For each identified node, a predicted biodiversity score was calculated from the plants design data. The scoring method accounts for the composition of plant species in that node – nodes with a higher proportion of wildlife-attracting plants (species that provide food or habitat for birds, insects, etc.) receive higher scores.
Expected Biodiversity Index: The result is a predicted biodiversity index for every node. This index represents the expected ecological performance of that node before observing the actual fauna. Essentially, it is a hypothesis of how well each patch should support biodiversity based on its vegetation characteristics.
Table: Node Attributes and Predicted Scores: Full table link here.
Nodes | Plants | Number | Bird-attracting | Butterfly/bee-attracting | Bat-attracting | Native | Per Plant Attractive Score | Total Plant Score | Node Score |
---|---|---|---|---|---|---|---|---|---|
Park P1 | CraC-4 | 1 | 0 | 1 | 0 | 1 | 1 | 1 | 1879 |
SamS-1 | 1 | 1 | 1 | 0 | 0 | 2 | 2 | ||
CraC-5 | 1 | 0 | 1 | 0 | 1 | 1 | 1 | ||
CraC-6 | 1 | 0 | 1 | 0 | 1 | 1 | 1 | ||
CaeF-1 | 1 | 1 | 1 | 0 | 0 | 2 | 2 | ||
CaeF-2 | 1 | 1 | 1 | 0 | 0 | 2 | 2 | ||
SyzL-1 | 1 | 1 | 1 | 0 | 1 | 2 | 2 | ||
SyzL-1 | 1 | 1 | 1 | 0 | 1 | 2 | 2 | ||
SyzL-1 | 1 | 1 | 1 | 0 | 1 | 2 | 2 | ||
SyzL-1 | 1 | 1 | 1 | 0 | 1 | 2 | 2 | ||
CaeF-3 | 1 | 1 | 1 | 0 | 0 | 2 | 2 | ||
MimE-2 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | ||
CaeF-4 | 1 | 1 | 1 | 0 | 0 | 2 | 2 | ||
CaeF-6 | 1 | 1 | 1 | 0 | 0 | 2 | 2 | ||
CaeF-5 | 1 | 1 | 1 | 0 | 0 | 2 | 2 | ||
CaeF-7 | 1 | 1 | 1 | 0 | 0 | 2 | 2 | ||
CraC-7 | 1 | 0 | 1 | 0 | 1 | 1 | 1 | ||
CraC-8 | 1 | 0 | 1 | 0 | 1 | 1 | 1 | ||
Asystasia gangetica | 90 | 1 | 1 | 0 | 0 | 2 | 180 | ||
Cyperus haspan | 40 | 0 | 0 | 0 | 0 | 0 | 0 | ||
Duranta erecta | 150 | 1 | 1 | 0 | 0 | 2 | 300 | ||
Ixora 'super king' | 150 | 1 | 1 | 0 | 0 | 2 | 300 | ||
Leucophyllum frutescens | 95 | 1 | 1 | 0 | 0 | 2 | 190 | ||
Loropetalum chinense | 175 | 1 | 0 | 0 | 0 | 1 | 175 | ||
Microsorum scolopendria | 50 | 0 | 0 | 0 | 1 | 0 | 0 | ||
Murraya paniculata | 100 | 1 | 1 | 0 | 0 | 2 | 200 | ||
Orthosiphon aristatus | 50 | 1 | 1 | 0 | 0 | 2 | 100 | ||
Pandanus amaryllifolius | 125 | 0 | 1 | 0 | 0 | 1 | 125 | ||
Pandanus pygmaeus | 80 | 0 | 0 | 0 | 0 | 0 | 0 | ||
Pennisetum setaceum | 80 | 1 | 1 | 0 | 0 | 2 | 160 | ||
Vitex ovata | 60 | 1 | 1 | 0 | 0 | 2 | 120 | ||
Park P2 | CitQ | 1 | 1 | 1 | 0 | 0 | 2 | 2 | 1788 |
CitQ | 1 | 1 | 1 | 0 | 0 | 2 | 2 | ||
CitQ | 1 | 1 | 1 | 0 | 0 | 2 | 2 | ||
CynM | 1 | 0 | 0 | 0 | 0 | 0 | 0 | ||
CynM | 1 | 0 | 0 | 0 | 0 | 0 | 0 | ||
CynM | 1 | 0 | 0 | 0 | 0 | 0 | 0 | ||
CynM | 1 | 0 | 0 | 0 | 0 | 0 | 0 | ||
CynM | 1 | 0 | 0 | 0 | 0 | 0 | 0 | ||
CynM | 1 | 0 | 0 | 0 | 0 | 0 | 0 | ||
CynM | 1 | 0 | 0 | 0 | 0 | 0 | 0 | ||
BucA | 1 | 1 | 1 | 1 | 1 | 3 | 3 | ||
BucA | 1 | 1 | 1 | 1 | 1 | 3 | 3 | ||
BucA | 1 | 1 | 1 | 1 | 1 | 3 | 3 | ||
BucA | 1 | 1 | 1 | 1 | 1 | 3 | 3 | ||
TriO | 1 | 0 | 0 | 0 | 1 | 0 | 0 | ||
TriO | 1 | 0 | 0 | 0 | 1 | 0 | 0 | ||
Arundina graminifolia | 110 | 0 | 1 | 0 | 1 | 1 | 110 | ||
Costus speciosus | 75 | 1 | 1 | 0 | 1 | 2 | 150 | ||
Cymbopogon citratus | 100 | 0 | 0 | 0 | 0 | 0 | 0 | ||
Cyperus alternifolius | 340 | 0 | 0 | 0 | 0 | 0 | 0 | ||
Donax grandis | 60 | 0 | 1 | 0 | 1 | 1 | 60 |
Biodiversity Field Survey: An on-site survey was carried out to collect observed biodiversity data for each node. Surveyors followed predefined transect routes through and around the building, systematically recording all plant and animal species present at each node and counting the number of individual organisms observed.
Empirical Biodiversity Index: From the survey data, actual biodiversity indices for each node were calculated. These empirical indices quantify the real biodiversity performance of each node. The collected data not only provide a basis for spatial mapping of biodiversity across the site, but also serve as ground truth for validating the predicted scores statistically.
Table: Survey Recording and Biodiversity Indices: Full table link here.
ID | Nodes | 0930Richness(species number) | 0930Abundance(individuals number) | 0930shannon diversity index(H) | 0930Shannon Equitability Index (Eh) | 1001Richness(species number) | 1001Abundance(individuals number) | 1001shannon diversity index(H) | 1001Shannon Equitability Index (Eh) | 1002Richness(species number) | 1002Abundance(individuals number) | 1002shannon diversity index(H) | 1002Shannon Equitability Index (Eh) | 1003Richness(species number) | 1003Abundance(individuals number) | 1003shannon diversity index(H) | 1003Shannon Equitability Index (Eh) | 1004Richness(species number) | 1004Abundance(individuals number) | 1004shannon diversity index(H) | 1004Shannon Equitability Index (Eh) | 1005Richness(species number) | 1005Abundance(individuals number) | 1005shannon diversity index(H) | 1005Shannon Equitability Index (Eh) | Average_Richness | Average_Abundance | Average_Shannon diversity(H) | Average_shannon equitability(Eh) |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
1 | park P1 | 2 | 7 | 0.410116318 | 0.591672779 | 5 | 21 | 1.210536763 | 0.75214878 | 2 | 7 | 0.598269589 | 0.863120569 | 5 | 15 | 1.337860678 | 0.831259577 | 1 | 8 | 0 | 0 | 4 | 7 | 1.277034259 | 0.921185497 | 3.166666667 | 10.83333333 | 0.805636268 | 0.659897867 |
2 | park P2 | 4 | 7 | 1.153741943 | 0.83224889 | 5 | 11 | 1.414279065 | 0.87874099 | 5 | 9 | 1.149059697 | 0.713950932 | 5 | 20 | 1.415022588 | 0.879202967 | 4 | 5 | 1.33217904 | 0.960964047 | 4 | 7 | 1.277034259 | 0.921185497 | 4.5 | 9.833333333 | 1.290219432 | 0.864382221 |
7 | park P7 | 4 | 5 | 1.33217904 | 0.960964047 | 2 | 5 | 0.500402424 | 0.721928095 | 6 | 31 | 1.42314131 | 0.794270288 | 5 | 17 | 1.466907105 | 0.91144063 | 6 | 37 | 0.993421665 | 0.554439188 | 7 | 56 | 1.426305017 | 0.732975784 | 5 | 25.16666667 | 1.19039276 | 0.779336339 |
8 | park P8 | 6 | 11 | 1.672625446 | 0.933510036 | 2 | 12 | 0.450561209 | 0.650022422 | 3 | 10 | 0.801818553 | 0.729846699 | 3 | 4 | 1.039720771 | 0.94639463 | 3 | 7 | 0.79631164 | 0.724834092 | 4 | 7 | 1.277034259 | 0.921185497 | 3.5 | 8.5 | 1.006345313 | 0.817632229 |
9 | park P9 | 2 | 5 | 0.673011667 | 0.970950594 | 4 | 8 | 1.073542846 | 0.77439747 | 3 | 5 | 1.054920168 | 0.960229718 | 3 | 7 | 1.078992208 | 0.982141033 | 2 | 3 | 0.636514168 | 0.918295834 | 3 | 4 | 1.039720771 | 0.94639463 | 2.833333333 | 5.333333333 | 0.926116971 | 0.925401547 |
10 | park P10 | 2 | 4 | 0.562335145 | 0.811278124 | 2 | 3 | 0.636514168 | 0.918295834 | 2 | 5 | 0.673011667 | 0.970950594 | 2 | 2 | 0.693147181 | 1 | 0 | 0 | 0 | 0 | 3 | 4 | 1.039720771 | 0.94639463 | 1.833333333 | 3 | 0.600788155 | 0.774486531 |
11 | park P11 | 4 | 8 | 1.386294361 | 1 | 2 | 4 | 0.693147181 | 1 | 3 | 11 | 0.759547391 | 0.69136983 | 5 | 8 | 1.559581156 | 0.969022256 | 4 | 9 | 1.149059697 | 0.828871363 | 2 | 5 | 0.673011667 | 0.970950594 | 3.333333333 | 7.5 | 1.036773576 | 0.910035674 |
6 | park P6 | 6 | 13 | 1.519382665 | 0.847983611 | 5 | 19 | 1.256637907 | 0.780793032 | 6 | 25 | 1.471602889 | 0.82131721 | 4 | 23 | 1.192258932 | 0.860033024 | 4 | 13 | 1.351681195 | 0.975031878 | 7 | 15 | 1.617053153 | 0.831000935 | 5.333333333 | 18 | 1.401436123 | 0.852693282 |
Right side present a semi-3D (2.5D) map of the building’s green infrastructure to visualize biodiversity data in context. This map displays each node’s predicted biodiversity score alongside its observed biodiversity index at the corresponding location (e.g. along different facade levels and site areas). The spatial visualization highlights where the design anticipated biodiversity “hotspots” and whether those areas actually exhibited high biodiversity on site, making any spatial discrepancies between expectation and reality immediately apparent.
A scatter chart plot the predicted biodiversity score of each node against its observed biodiversity index. This visualization directly shows the correlation between design expectations and real outcomes. Notably, the data points cluster along a downward-sloping trend line – a clear negative correlation. In other words, nodes that were predicted to have higher biodiversity often turned out to have lower biodiversity in reality, and vice versa. This negative trend indicates that the vertical greenery design underperformed relative to expectations: the intended biodiversity benefits were not realized to the extent predicted. The scatter plot thus serves as a crucial reality check, revealing the gap between the model’s predictions and the actual ecological performance measured on site.