Day 8 part 1 C,N,P, Anammox

Environmental Biotechnology

🌍 Overview

This lecture focused on the nitrogen cycle and its relation to resource recovery and pollution control — particularly in wastewater treatment.

Two main parts:

  1. The nitrogen cycle in nature and technology
  2. Nitrogen removal and recovery processes in wastewater treatment plants (WWTPs)

⚗️ The Nitrogen Cycle

🧩 Main Processes

  1. Nitrogen fixation
    • Conversion of atmospheric N₂ → ammonia (NH₃).
    • Occurs naturally (microbes, lightning) and artificially via the Haber-Bosch process.
  2. Nitrification
    • Oxidation of ammonia → nitrite (NO₂⁻) → nitrate (NO₃⁻).
    • Two groups of bacteria:
      • AOB (Ammonia-oxidizing bacteria): e.g., Nitrosomonas
      • NOB (Nitrite-oxidizing bacteria): e.g., Nitrospira, Nitrobacter
  3. Denitrification
    • Reduction of NO₃⁻ → NO₂⁻ → NO → N₂O → N₂ gas
    • Removes nitrogen from ecosystems; produces greenhouse gas N₂O.
  4. DNRA (Dissimilatory Nitrate Reduction to Ammonium)
    • Converts nitrate → ammonia instead of nitrogen gas.
  5. Anammox (Anaerobic Ammonium Oxidation)
    • NH₄⁺ + NO₂⁻ → N₂ + H₂O
    • Carried out by Planctomycetes (e.g., Brocadia, Kuenenia).
    • Energy-efficient, no organic carbon needed.

🧪 Importance of Haber–Bosch

The Haber–Bosch process revolutionized agriculture by producing massive amounts of ammonia for fertilizers. ➡️ Enabled human population growth (roughly half of global nitrogen now synthetic). But also:

  • 💀 Causes eutrophication in lakes & seas
  • 🏭 Adds nitrogen pollution from agriculture and fossil fuels

🚰 Nitrogen in Wastewater

  • Typical municipal wastewater contains 30–50 mg N/L.
  • EU limit: <8 mg/L discharge.
  • Each person produces ~4.4 kg nitrogen/year in wastewater.

🧴 Nitrogen Recovery (rarely done)

  • Possible by:
    • Air stripping: raise pH to volatilize ammonia (inefficient).
    • Struvite precipitation: MgNH₄PO₄·6H₂O crystallization.
    • Single-cell protein production: bacteria grown on methane + ammonia.
  • Usually not done because the Haber–Bosch route is cheaper.

🧫 Nitrification in Depth

Key Bacteria

  • AOB: Nitrosomonas, Nitrosospira
  • NOB: Nitrospira, Nitrotoga, Nitrobacter

Nitrospira are slow-growing, oxygen-sensitive, and require long sludge ages (10–20 days in cold climates).

Temperature effects:

  • Warm (e.g., tropics): 5 days sludge age
  • Cold (e.g., Finland): up to 20 days

🧠 COMAMMOX (Complete Ammonia Oxidizers)

  • Discovery: Nitrospira inopinata (“surprising spiral”)
  • Can oxidize ammonia → nitrate in one organism (no separate AOB/NOB).
  • Discovered via genome sequencing of full nitrification reactors that lacked AOBs.
  • Advantages:
    • High ammonia affinity
    • No N₂O production
    • Efficient at low concentrations
  • Rare in Danish WWTPs (found in Ribe, Haderslev, etc.)

🧬 Denitrification

Steps:

  1. NO₃⁻ → NO₂⁻ (nitrate reductase)
  2. NO₂⁻ → NO (nitrite reductase)
  3. NO → N₂O (nitric oxide reductase)
  4. N₂O → N₂ (nitrous oxide reductase)

Each step handled by different enzymes and often different microbes. → Most species only perform part of the pathway.

Conditions:

  • No oxygen (anoxic)
  • Organic carbon as electron donor
  • pH rises (opposite to nitrification)

Environmental issue: N₂O (nitrous oxide) is a potent greenhouse gas. Some Danish WWTPs face fines if emissions exceed limits.


🧫 Typical WWTP Designs

1. Two-stage system

  • Tank 1: Nitrification (with O₂)
  • Tank 2: Denitrification (without O₂ + organics added, e.g., methanol)

2. Modern single-sludge system (recirculating)

  • Denitrification happens first using organics from wastewater
  • Nitrification follows
  • Nitrate-rich water is recirculated back
  • ⚙️ Internal circulation keeps nitrates available for denitrification

Key parameters:

  • Recirculation rate ≈ 6× inflow
  • Requires balance between oxygen levels, organics, and sludge retention

🔴 Anammox Process in Practice

Features:

  • Found in oxygen-free zones of sediments and reactors.
  • Red cells due to anammoxosome organelle (contains rocket-fuel-like hydrazine!).
  • Grow very slowly (doubling time ≈ 10 days).

Implementation:

  1. Two-step system: partial nitrification → anammox
  2. Single-reactor (SHARON-Anammox):
    • Limit oxygen so only ammonia → nitrite
    • Anammox bacteria convert NH₄⁺ + NO₂⁻ → N₂
    • No organic carbon needed

Advantages:

  • ~50% less oxygen demand
  • No carbon addition
  • Lower sludge production

Challenges:

  • Complex control (oxygen, temperature)
  • Sensitive to disturbances
  • Works best in warm, stable conditions

🇩🇰 Denmark’s Success Story

  • Denmark introduced large-scale nitrogen removal ~30 years ago.
  • One of the most effective countries worldwide.
  • Now exploring Anammox-based systems to further cut costs and emissions.

🧭 Summary of Key Takeaways

ConceptDescriptionImportance
Nitrogen fixationN₂ → NH₃ (biological or Haber–Bosch)Supports agriculture, causes runoff
NitrificationNH₃ → NO₂⁻ → NO₃⁻Aerobic, slow, oxygen-sensitive
DenitrificationNO₃⁻ → N₂Removes nitrogen gas, produces N₂O
AnammoxNH₄⁺ + NO₂⁻ → N₂Anaerobic, energy-saving
COMAMMOXSingle organism does full oxidationEfficient, low N₂O emission
WWTP designCoupled nitrification/denitrification or AnammoxDetermines energy use and N removal
Danish approachStrict N regulations + innovationGlobal model for nutrient removal

Quiz

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