Final Project: Landscape Practice for Biodiversity in Vertical Greenery

Empirical Mapping Biodiversity Assessment of 3D Ecological Performance

By Ren Junyao

Assignment 5 link: Please open the link, download and view.

Research Context

Background:

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.

Research Question:

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.

Case Study Site:

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.

Wilmar Building View 1
Wilmar Building View 1
Wilmar Building View 2
Wilmar Building View 2
Site Garden View 1
Site Garden View 1
Site Garden View 2
Site Garden View 2

Node Definition and Predicted Biodiversity Scores

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 P1CraC-410101111879
SamS-11110022
CraC-51010111
CraC-61010111
CaeF-11110022
CaeF-21110022
SyzL-11110122
SyzL-11110122
SyzL-11110122
SyzL-11110122
CaeF-31110022
MimE-21000000
CaeF-41110022
CaeF-61110022
CaeF-51110022
CaeF-71110022
CraC-71010111
CraC-81010111
Asystasia gangetica9011002180
Cyperus haspan40000000
Duranta erecta15011002300
Ixora 'super king'15011002300
Leucophyllum frutescens9511002190
Loropetalum chinense17510001175
Microsorum scolopendria50000100
Murraya paniculata10011002200
Orthosiphon aristatus5011002100
Pandanus amaryllifolius12501001125
Pandanus pygmaeus80000000
Pennisetum setaceum8011002160
Vitex ovata6011002120
Park P2CitQ11100221788
CitQ1110022
CitQ1110022
CynM1000000
CynM1000000
CynM1000000
CynM1000000
CynM1000000
CynM1000000
CynM1000000
BucA1111133
BucA1111133
BucA1111133
BucA1111133
TriO1000100
TriO1000100
Arundina graminifolia11001011110
Costus speciosus7511012150
Cymbopogon citratus100000000
Cyperus alternifolius340000000
Donax grandis600101160
L1 and Park Nodes
L1 and Park Nodes
L3 Nodes
L3 Nodes
L4 Nodes
L4 Nodes
L5 Nodes
L5 Nodes
L6 Nodes
L6 Nodes
L7 Nodes
L7 Nodes

On-Site Survey and Results

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)
1park P1270.4101163180.5916727795211.2105367630.75214878270.5982695890.8631205695151.3378606780.8312595771800471.2770342590.9211854973.16666666710.833333330.8056362680.659897867
2park P2471.1537419430.832248895111.4142790650.87874099591.1490596970.7139509325201.4150225880.879202967451.332179040.960964047471.2770342590.9211854974.59.8333333331.2902194320.864382221
7park P7451.332179040.960964047250.5004024240.7219280956311.423141310.7942702885171.4669071050.911440636370.9934216650.5544391887561.4263050170.732975784525.166666671.190392760.779336339
8park P86111.6726254460.9335100362120.4505612090.6500224223100.8018185530.729846699341.0397207710.94639463370.796311640.724834092471.2770342590.9211854973.58.51.0063453130.817632229
9park P9250.6730116670.970950594481.0735428460.77439747351.0549201680.960229718371.0789922080.982141033230.6365141680.918295834341.0397207710.946394632.8333333335.3333333330.9261169710.925401547
10park P10240.5623351450.811278124230.6365141680.918295834250.6730116670.970950594220.69314718110000341.0397207710.946394631.83333333330.6007881550.774486531
11park P11481.3862943611240.69314718113110.7595473910.69136983581.5595811560.969022256491.1490596970.828871363250.6730116670.9709505943.3333333337.51.0367735760.910035674
6park P66131.5193826650.8479836115191.2566379070.7807930326251.4716028890.821317214231.1922589320.8600330244131.3516811950.9750318787151.6170531530.8310009355.333333333181.4014361230.852693282
Survey Transects Route
Survey Transects Routes

Interactive 2.5D Biodiversity Visualization & Statistical Analysis

2.5D Interactive Spatial Map:

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.

Scatter Plot (Prediction vs. Observation):

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.

Implications and Future Strategies:

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