Aim:
To estimate the plant and animal biodiversity of the college campus using quadrat and transect sampling methods and to calculate the Simpson's Biodiversity Index for different habitats.
1) Biodiversity assessment tool
Principle:
Biodiversity encompasses the variety of life at all levels. Assessing it requires sampling methods because counting every individual in a large area is impossible. For immobile organisms (plants), quadrat sampling is used. For mobile organisms (insects, birds), transect walks and direct observation are effective. The data collected is used to calculate diversity indices, which provide a quantitative measure that combines both species richness (number of species) and species evenness (abundance of each species). The most common is Simpson's Biodiversity Index (D).
Materials Required:
1m x 1m Quadrat frame (can be made with sticks and rope)
Measuring tape (50m)
Field notebook and pencil
Camera or smartphone (for documenting species)
Local field guides or identification apps (e.g., Google Lens, iNaturalist, PlantNet)
Sweep net (for insects)
Binoculars (for birds)
Procedure:
Step 1: Define Habitats and Hypothesis
Identify and mark 2-3 distinct habitats on your campus map:
Manicured Lawn: Regularly mowed grass area.
Wooded Area: Area with trees and undergrowth.
Gardened Area: Flower beds or landscaped sections.
Formulate a Hypothesis: "The wooded area will have higher plant and animal biodiversity compared to the manicured lawn."
Step 2: Plant Biodiversity Sampling (Quadrat Method)
Random Placement: In each habitat, use a "random walk" method or generate random coordinates to place the 1m² quadrat at 5 different locations.
Identify and Count: For each quadrat:
Identify all plant species within the frame.
For each species, estimate its percentage cover (e.g., Grass: 70%, Clover: 20%, Dandelion: 10%).
Record the data in a table.
Step 3: Animal Biodiversity Sampling (Transect Walk)
Define the Transect: Lay a 50m measuring tape in a straight line through each habitat.
Walk and Observe: Walk slowly along the tape for 15 minutes.
Record all animal species seen or heard (birds, insects, reptiles, mammals) within 5m on either side of the tape.
For insects, use a sweep net (10 sweeps per habitat).
Tally the number of individuals of each species.
Step 4: Data Analysis
Calculate Species Richness (S): The total number of different species found in each habitat.
Calculate Simpson's Biodiversity Index (D): This measures the probability that two individuals randomly selected from a sample will belong to the same species. A higher value (closer to 1) indicates greater diversity.
Formula:n= total number of individuals (or % cover) of a particular speciesN= total number of individuals (or total % cover) of all species∑= sum of the calculations for each species
Observations:
Table 1: Plant Species Data from Manicured Lawn Habitat (Quadrat Sampling)
| Species Name | % Cover (n) | n(n-1) |
|---|---|---|
| Bermuda Grass | 70 | 70*69 = 4830 |
| White Clover | 20 | 20*19 = 380 |
| Plantain | 10 | 10*9 = 90 |
| Total (N) | 100 | ∑ = 5300 |
Table 2: Animal Species Data from Wooded Habitat (Transect Walk)
| Species Name | Abundance (n) | n(n-1) |
|---|---|---|
| Ants | 45 | 45*44 = 1980 |
| Earthworm | 10 | 10*9 = 90 |
| Sparrow | 3 | 3*2 = 6 |
| Squirrel | 2 | 2*1 = 2 |
| Total (N) | 60 | ∑ = 2078 |
Calculations:
1. Simpson's Index (D) for Lawn Plants:
2. Simpson's Index (D) for Wooded Area Animals:
Result:
The plant biodiversity in the lawn habitat, as measured by Simpson's Index, is 0.465.
The animal biodiversity in the wooded habitat, as measured by Simpson's Index, is 0.413.
Species Richness: The wooded area had a higher number of animal species (S=4) compared to the lawn (S=3 for plants in this sample).
The hypothesis was partially supported: The wooded area showed higher species richness, but the Simpson's Index for the lawn was slightly higher due to the high evenness of three species, compared to the ant-dominated animal community in the woods.
Discussion:
Interpretation of Results: The lawn's plant diversity was moderate. While it had fewer species, the evenness was high. The wooded area supported more animal species, but the community was dominated by ants, which lowered its diversity index.
Urban Biodiversity: This study highlights that even small, managed ecosystems like a college campus host measurable biodiversity. The presence of squirrels and diverse insects indicates the ecological value of urban green spaces.
Limitations: Sampling bias (weather, time of day), misidentification of species, and the small sample size are limitations. Many nocturnal and cryptic species were missed.
Importance: Understanding local biodiversity is the first step toward conservation. This method can be used to monitor changes over time and assess the impact of campus management practices.
Conclusion:
The quadrat and transect methods are efficient and practical tools for estimating local biodiversity. The calculation of Simpson's Diversity Index provides a quantitative measure to compare different habitats. This study successfully documented and quantified the plant and animal life on the college campus, revealing that both manicured and naturalized areas contribute to its overall ecological value. Conserving even small wooded patches is crucial for maintaining urban biodiversity.
Viva Voce Questions:
Why is a quadrat used for plants and a transect for animals?
Plants are sessile (immobile), so a quadrat provides a snapshot of a fixed area. Animals are mobile, so a transect walk is better for capturing their presence along a path.
What does a Simpson's Index value of 0 mean? What does a value of 1 mean?
0 indicates no diversity (only one species present). 1 indicates infinite diversity (every individual belongs to a different species).
Name one reason why a managed lawn might have lower biodiversity than a wild meadow.
Regular mowing prevents the growth of flowering herbs and shrubs, reducing habitat and food sources for many species.
How could you improve the accuracy of this study?
By increasing the sample size (more quadrats/transects), repeating the study in different seasons, and involving experts for accurate species identification.
What is the difference between species richness and species evenness?
Richness is the total number of different species. Evenness is how close in numbers the populations of each species are. Simpson's Index combines both.
B
Practical Manual: Digital-Integrated Biodiversity Assessment of College Campus
Aim
To estimate plant and animal biodiversity of the college campus using quadrat and transect sampling methods, document observations through iNaturalist, and calculate Simpson's Biodiversity Index for different habitats.
Learning Objectives
Upon completion, students will be able to:
Execute systematic quadrat and transect sampling protocols
- Utilize iNaturalist for species documentation, identification, and data verification
- Calculate and interpret Simpson's Biodiversity Index across habitats
- Contribute to global biodiversity databases through citizen science
- Analyze spatial distribution patterns using digital mapping tools
- Evaluate data quality and observer bias in citizen science platform
Theoretical Background
1. Traditional Sampling Methods + Digital Enhancement
Traditional Method
Digital Integration via iNaturalist
Advantage
Field notebooks
Mobile app observations with GPS coordinates
Permanent georeferenced records
Physical voucher specimens
Research-grade photo vouchers
Non-destructive documentation
Expert identification
Community/CV-assisted ID + expert verification
Faster, accessible taxonomy
Manual data entry
Automatic database export (CSV/JSON)
Error reduction, time efficiency
Local reports
Global biodiversity data contribution
Real-world impact, open science
2. iNaturalist as a Scientific Tool
Research Grade Observations: Require date, location, photo evidence, and community verification
Computer Vision: AI suggestions trained on millions of observations
Data Quality: Community consensus mechanism; experts can confirm/refine IDs
Export Capabilities: CSV download for statistical analysis (abundance, frequency data)
3. Simpson's Diversity Index (D)
Materials Required
| Category | Items |
|---|---|
| Digital Equipment | Smartphone with camera, portable charger, iNaturalist app (installed), GPS/location services enabled |
| Field Equipment | Quadrat frames (0.5m × 0.5m, 1m × 1m), measuring tape (30-50m), compass, flag markers |
| Documentation | Field notebook (backup), data sheets, clipboard, waterproof labels for physical vouchers |
| Physical Collection | Plant press (optional backup), insect aspirator (if permitted), 70% ethanol, ziplock bags |
| Safety | First aid kit, sunscreen, insect repellent, water, sturdy footwear |
Pre-Field Preparation: iNaturalist Setup
Step 1: Account Creation & Project Setup
- Download iNaturalist app (iOS/Android) or visit https://www.inaturalist.org
- Create student account using institutional email
- Join your class project: "[College Name] Biodiversity Assessment 2024"
- Configure settings:
- Location accuracy: High precision (GPS on)
- License: CC-BY for educational use
- Data sharing: Enable automatic sync
Step 2: Pre-Field Training
- Complete iNaturalist "Getting Started" tutorial
- Practice photographing: Whole organism + Habitat + Diagnostic features (leaves, flowers, bark)
- Review taxonomy: Kingdom → Species identification levels
- Understand "Research Grade" criteria:
- ✓ Date and location present
- ✓ Photo/media evidence
- ✓ Not captive/cultivated (wild organisms only)
- ✓ Community ID agreement at species level
Experimental Design
Study Site Selection
| Habitat Code | Description | iNaturalist Place Filter |
|---|---|---|
| H1-LAWN | Maintained grass/turf areas | Campus lawns, open green |
| H2-WOOD | Native/exotic tree grove | Woodland, arboretum |
| H3-GARD | Flower beds, landscaped areas | Botanical garden sections |
| H4-DIST | Disturbed/construction edges | Brownfield, roadside verges |
Methodology
Part A: Quadrat Sampling with iNaturalist Documentation
Procedure:
- Establish 50m × 50m representative plot in each habitat
- Use random coordinates to place 10 quadrats (1m × 1m) per habitat
- Minimum 5m spacing between quadrats
| Step | Action | iNaturalist Function |
|---|---|---|
| 1 | Photograph entire plant/animal in situ | Add observation → Take photo |
| 2 | Capture diagnostic features (leaf, flower, bark, tracks) | Add multiple photos to single observation |
| 3 | Record exact count/abundance in Notes field | Observation Notes: "Quadrat Q1-LAWN, n=15 individuals" |
| 4 | Tag with project and habitat code | Projects → "[College] Biodiversity Assessment" |
| 5 | Mark location with high accuracy (<10m radius) | Verify GPS pin placement |
| 6 | Initial ID to lowest possible taxon | Use AI suggestions or field guides |
| Quadrat | iNaturalist Obs. ID | Species (App Suggestion) | Community ID | Individuals (n) | % Cover | Research Grade? |
|---|---|---|---|---|---|---|
| Q1-LAWN | [URL/ID] | Cynodon dactylon | Cynodon dactylon | 45 | 60% | ✓ Yes |
| Q1-LAWN | [URL/ID] | Trifolium sp. | Trifolium repens | 8 | 15% | ✓ Yes |
- Review iNaturalist notifications for community feedback
- Update IDs based on expert suggestions
- Withdraw incorrect observations to maintain data quality
Part B: Transect Sampling with iNaturalist
Procedure:
- 100m line transect per habitat (compass-oriented)
- Belt width: 2m (1m each side of center line)
- Mark every 10m with GPS waypoints
- Mobile App Method: Create observations continuously while walking
- Effort: Slow walk (10m per 2 minutes) to ensure detection
- Documentation: Every distinct species encountered gets observation
- Abundance: Use iNaturalist "Number of individuals" field or Notes
| Taxon | Detection Method | iNaturalist Evidence |
|---|---|---|
| Birds | Visual/audial | Photo, sound recording, or field notes with description |
| Insects | Hand capture → photo → release | Macro photography, habitat notes |
| Mammals | Indirect (tracks, scat, burrows) | Photograph sign, measure, scale object |
| Herps | Visual encounter | Habitat photo, dorsal/lateral views |
- Conduct 3 replicate surveys per habitat
- Vary times: Morning (6-9 AM), Midday (12-2 PM), Evening (4-7 PM)
- iNaturalist automatically timestamps observations
Part C: Data Export from iNaturalist for Analysis
Step 1: Filter Observations
- Apply filters:
- Project: [Your Class Project]
- Observer: Your username or group members
- Quality Grade: Research Grade (for verified data)
- Date: Survey dates
Step 2: Export Data
- Click "Download" → Create export
- Select fields:
id,observed_on,url,image_url,sound_url,description,num_identification_agreements,taxon_id,scientific_name,common_name,iconic_taxon_name,taxon_family_name,latitude,longitude,positional_accuracy,place_guess
Step 3: Data Cleaning
- Import CSV to Excel/R/Python
- Extract abundance data from "Description" field (if recorded as "n=15")
- Cross-reference with field notebook backup data
- Resolve any "Needs ID" observations manually using field guides
Part D: Simpson's Biodiversity Index Calculation
Using iNaturalist Data:
| iNaturalist ID | Species (Community ID) | Family | Individuals (n) | |
|---|---|---|---|---|
| obs/123456 | Cynodon dactylon | Poaceae | 45 | 1,980 |
| obs/123457 | Trifolium repens | Fabaceae | 12 | 132 |
| obs/123458 | Plantago major | Plantaginaceae | 8 | 56 |
| obs/123459 | Euphorbia hirta | Euphorbiaceae | 5 | 20 |
| obs/123460 | Cyperus rotundus | Cyperaceae | 3 | 6 |
| Total | S = 5 species | N = 73 | Σ = 2,194 |
Advanced: iNaturalist API for Automated Analysis
# Optional: Use iNaturalist API to fetch observations programmatically
import requests
params = {
'project_id': 'your-project-id',
'quality_grade': 'research',
'iconic_taxa': 'Plantae'
}
response = requests.get('https://api.inaturalist.org/v1/observations', params=params)
data = response.json()
# Process for Simpson's Index calculationData Analysis & Comparison
Comparative Analysis Table:
| Metric | Lawn | Woodland | Garden | Disturbed | Calculation Source |
|---|---|---|---|---|---|
| Total Observations | 45 | 78 | 52 | 31 | iNaturalist count |
| Research Grade % | 89% | 94% | 85% | 71% | Data quality check |
| Species Richness (S) | 8 | 22 | 15 | 6 | Unique taxa |
| Total Individuals (N) | 156 | 203 | 98 | 42 | Sum of abundances |
| Simpson's D | 0.42 | 0.15 | 0.28 | 0.55 | Formula |
| Simpson's 1-D | 0.58 | 0.85 | 0.72 | 0.45 | Diversity index |
| Dominant Species | Cynodon (29%) | Shorea (12%) | Rosa (18%) | Chenopodium (35%) | % of N |
| Evenness (J) | 0.65 | 0.88 | 0.78 | 0.52 |
iNaturalist-Specific Metrics:
| Metric | Description | Interpretation |
|---|---|---|
| ID Agreement Ratio | Agreements/Total IDs | Higher = more confident taxonomy |
| Taxon Ranks | % ID to Species vs. Genus/Family | Indicates identification difficulty |
| Spatial Accuracy | Mean positional accuracy (m) | <30m = reliable for campus scale |
| Temporal Distribution | Observations across time periods | Detects phenological patterns |
Integration of iNaturalist Features
1. Computer Vision vs. Expert Verification
- Compare your initial ID (AI suggestion) with final Community ID
- Calculate Accuracy Rate:
- Discuss: When does AI fail? (rare species, poor photos, juvenile stages)
2. Range Maps & Species Occurrence
- Use iNaturalist "Map" view to see if species are novel to campus
- Check "Seen Nearby" feature for expected species not detected
- Compare campus list with regional species pool
3. Phenology Analysis
- iNaturalist automatically records flowering/fruiting if annotated
- Filter by "Flowering" observation field
- Compare phenology across habitats
Expected Results & Digital Insights
Habitat Patterns:
| Habitat | Expected Pattern | iNaturalist Insight |
|---|---|---|
| Lawn | Low diversity, high dominance | Many "Casual" grade (cultivated grass); few Research Grade natives |
| Woodland | Highest diversity, complex structure | High insect/bird diversity; seasonal variation visible in timeline |
| Garden | Moderate diversity, exotic bias | Many "Captive/Cultivated" flags; compare wild vs. planted |
| Disturbed | Pioneer species, low evenness | Early successional specialists; iNaturalist may suggest weedy natives |
Data Quality Considerations:
- Observer Bias: Are showy flowers over-represented?
- Detection Bias: Do small insects achieve Research Grade less often than birds?
- Temporal Bias: Are nocturnal species under-sampled?
Precautions & Best Practices
| Issue | iNaturalist Solution | Traditional Backup |
|---|---|---|
| No internet in field | App works offline; sync later | Field notebook mandatory |
| Battery failure | Portable charger; airplane mode between obs | Physical data sheets |
| Taxonomic uncertainty | ID to genus/family; mark "ID Please" | Collect voucher (if permitted) |
| Location sensitivity | Obscure location for rare species (if any) | General place name only |
| Photo quality | Multiple angles; scale object; focus | Sketch diagnostic features |
Discussion Questions
Methodological:
- How does iNaturalist's "Research Grade" filter affect biodiversity estimates? What biases might this introduce?
- Compare the time efficiency of digital documentation vs. traditional voucher collection. What is lost/gained?
- How does community identification accuracy vary across taxonomic groups (plants vs. insects vs. fungi)?
Ecological:
- Analyze your Simpson's Index results: Which habitat has highest diversity? Does this align with structural complexity?
- Use iNaturalist "Compare" tool: Are campus species distributions expanding or contracting based on historical observations?
Citizen Science:
- How does your class data contribute to global biodiversity monitoring (e.g., GBIF, conservation assessments)?
- Discuss privacy implications of precise geotagging for rare species on campus.
Deliverables
Individual Submission:
- iNaturalist Profile: Minimum 50 Research Grade observations
- Data Export: CSV of all observations with metadata
- Calculations: Simpson's Index for assigned habitat (hand calculations + spreadsheet)
- Species Portfolio: 5 best-documented species with natural history notes
Group Report (4-5 students):
- Comparative Analysis: 3000-word report including:
- Methodology (traditional + digital integration)
- Results (tables, figures from iNaturalist data)
- Habitat comparison using Simpson's Index
- Data quality assessment
- Visualizations:
- iNaturalist "Observations Map" screenshot
- Species accumulation curves
- Rank-abundance diagrams
- Management Recommendations: Based on biodiversity hotspots identified
Assessment Rubric
| Criteria | Excellent (9-10) | Good (7-8) | Satisfactory (5-6) | Poor (<5) |
|---|---|---|---|---|
| iNaturalist Proficiency | 50+ Research Grade, accurate IDs, full metadata | 40+ obs, mostly Research Grade, minor errors | 30+ obs, some quality issues | <30 obs, many casual grade |
| Field Execution | Systematic sampling, GPS accuracy <10m, replicate surveys | Good methodology, minor GPS errors | Some systematic bias | Unreliable sampling |
| Data Analysis | Correct Simpson's calculations, comparative statistics, error analysis | Correct calculations, basic comparison | Calculation errors, superficial | Incorrect methodology |
| Integration | Insightful discussion of digital vs. traditional methods | Good comparison of approaches | Limited critical analysis | No digital integration discussion |
| Contribution | Active community ID, project curation, data quality flags | Some community engagement | Passive observation only | No iNaturalist engagement |
References & Resources
- iNaturalist:
- Website: https://www.inaturalist.org
- Teacher's Guide: https://www.inaturalist.org/pages/teacher's+guide
- API Documentation: https://api.inaturalist.org/v1/docs/
- Ecological Methods:
- Magurran, A.E. (2004). Measuring Biological Diversity. Blackwell.
- Krebs, C.J. (1999). Ecological Methodology (2nd ed.).
- Citizen Science:
- Chandler et al. (2017). Contribution of citizen science toward international biodiversity monitoring. Biological Conservation.
Duration: 8 hours field work + 6 hours digital
curation/analysis
Technology Requirement: Smartphone per student, iNaturalist account
Data Legacy: All Research Grade observations permanently contribute to GBIF and
conservation science
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