The lecture focuses on the 16S rRNA gene — the genetic “fingerprint” used to identify bacteria.
If your sample is unrepresentative, your entire analysis is meaningless. Key considerations:
💧 Example (Wastewater Treatment Plant): Multiple bioreactors were sampled (B1–B5).
Samples can degrade!
Key factor: Bead-beating intensity (cell lysis).
Use FISH (Fluorescence In Situ Hybridization) 🧪
Primers determine which bacteria you can detect.
Check primer coverage in silico using tools like SILVA TestPrime or MiDAS databases. 💡 Example: V3–V4 underestimates Chloroflexi — a key phylum in wastewater plants.
PCR optimization:
Many bacteria have more than one copy of the 16S gene.
Sources of bias:
| Method | Description | Pros | Cons |
|---|---|---|---|
| OTUs | Clusters at 97% similarity | Handles few samples well | Lower precision |
| ASVs | 100% identical sequences | High resolution, reproducible | Needs many samples |
🧠 Tip: Use ASVs when possible for reproducible, fine-scale taxonomy.
Databases (SILVA, MiDAS, etc.) are used to match 16S reads.
If unclassified:
Use ecosystem-specific databases (like MiDAS for wastewater). They provide:
The 16S dataset gives relative abundance, not true absolute abundance.
Even with all limitations, 16S sequencing is powerful when applied correctly.
MiDAS (Microbial Database for Activated Sludge)
Each wastewater plant has a unique microbial fingerprint. Differences arise from:
Researchers transplanted microbial communities from a healthy plant to a failing one.
Portable devices allow on-site DNA sequencing in real time. Potential: biological sensors for monitoring plant health.
Long-term monitoring enables machine learning predictions.
Despite many sources of bias and uncertainty:
16S rRNA gene sequencing works beautifully when paired with good sampling, thoughtful design, and validation.
It provides insight into “who is there” — the microbial ecology — forming the foundation for functional understanding, prediction, and control in environmental biotechnology. 🌿🧬💧