Acid Mine Drainage (AMD) – Causes, Impacts & Control Measures | DGMS Notes

Acid Mine Drainage (AMD) – Causes, Impacts & Control Measures | DGMS Notes

⚗️ Acid Mine Drainage (AMD): Causes, Impacts & Control Measures

🧭 1. Detailed Notes (As per DGMS & Environmental Standards)

1.1 Introduction

Acid Mine Drainage (AMD) refers to the outflow of acidic water from coal or metal mines where sulphide minerals (mainly pyrite – FeS₂) are exposed to air and water.

When these minerals oxidize, sulphuric acid and dissolved metals are released, causing severe environmental contamination. This phenomenon is common in coalfields like Jharia, Raniganj, and Singrauli, and metallic mines such as zinc, copper, and iron ore mines.

1.2 Chemical Reaction of AMD Formation

Step 1: Oxidation of Pyrite
FeS₂ + 3.5O₂ + H₂O → Fe²⁺ + 2SO₄²⁻ + 2H⁺

Step 2: Further Oxidation
Fe²⁺ + 0.25O₂ + H⁺ → Fe³⁺ + 0.5H₂O

Step 3: Ferric Iron Hydrolysis
Fe³⁺ + 3H₂O → Fe(OH)₃↓ + 3H⁺

Result: Continuous regeneration of acid and iron hydroxides → water pH drops below 3.

1.3 Causes of AMD

  • Oxidation of sulphide minerals (especially pyrite) in exposed rock surfaces.
  • Mining-induced fracturing that increases permeability to oxygen and water.
  • Poor waste rock management allowing rain infiltration.
  • Abandoned mines without closure measures.
  • Lack of neutralization or water treatment facilities.

1.4 Environmental Impacts

  • Surface and groundwater contamination due to low pH (<4).
  • Heavy metal leaching – Fe, Mn, Al, Zn, Cu, Pb contaminate streams.
  • Destruction of aquatic life – fish kills, loss of biodiversity.
  • Soil acidification, affecting vegetation and agriculture.
  • Corrosion of mine equipment and pipelines.
  • Violation of DGMS and CPCB environmental discharge norms.

1.5 Regulatory Framework

DGMS and MOEFCC require mines to ensure:

  • Zero discharge of untreated mine water.
  • Compliance with Water (Prevention and Control of Pollution) Act, 1974.
  • Monitoring under CMR 2017 Regulation 131 (Discharge of mine water).
  • AMD management included in Mine Closure Plan as per MCDR 2017.

1.6 Control & Prevention Measures

A. Source Control

  • Backfilling & Water Cover: Reduces oxygen contact with pyritic materials.
  • Sealing of old workings: Prevents infiltration.
  • Covering waste dumps: With clay, topsoil, or geomembrane.
  • Alkaline addition in overburden: Mix limestone to neutralize acid.

B. Chemical Treatment

  • Neutralization with lime, limestone, or soda ash:
    CaCO₃ + 2H⁺ → Ca²⁺ + CO₂ + H₂O
  • Aeration tanks: Oxidize Fe²⁺ to Fe³⁺ before settling.
  • Precipitation of metals: Fe(OH)₃, Al(OH)₃ removal via sedimentation.

C. Biological Treatment

  • Constructed wetlands: Use sulphate-reducing bacteria (SRB) to form FeS precipitates.
  • Anaerobic bioreactors: Organic substrate + bacteria = sulphate reduction.
  • Passive treatment: Long-term, low-maintenance AMD control system.

D. Physical Measures

  • Diversion drains around dumps.
  • Lined collection ponds.
  • Proper grading and water management in mine dumps.

1.7 Typical AMD Treatment Flow

Mine Water ➜ Collection Sump ➜ Neutralization Tank ➜ Aeration ➜ Sedimentation ➜ Constructed Wetland ➜ Discharge/Recycling

1.8 DGMS Circulars & Standards

  • DGMS Circular No. 1 of 1978: Pumping and water handling safety.
  • DGMS Circular No. 2 of 1984: Sedimentation pond design.
  • CPCB Norms: pH 6.5–8.5 for discharge, TSS < 100 mg/L, Fe < 3 mg/L.

⚡ 2. Quick One-Liners (Revision Points)

  • AMD mainly forms due to oxidation of pyrite (FeS₂).
  • pH of AMD water can drop below 3.
  • Fe³⁺ acts as a catalyst in AMD formation.
  • Lime neutralization increases pH rapidly.
  • Constructed wetlands use sulphate-reducing bacteria.
  • Limestone drains are passive AMD treatment.
  • pH <4 water is unsafe for aquatic life.
  • DGMS Reg.131 governs mine water discharge.
  • CPCB discharge pH range = 6.5–8.5.
  • Backfilling with inert material prevents AMD formation.

🧾 3. Descriptive Model Answer

Q: Explain the causes, impacts, and control measures of Acid Mine Drainage (AMD) in mines.

Model Answer:

Acid Mine Drainage (AMD) occurs when sulphide minerals like pyrite (FeS₂) oxidize in contact with air and water, producing sulphuric acid and soluble iron. The process lowers pH and leaches heavy metals.

Environmental impacts include contamination of streams, soil acidification, and aquatic life destruction.

AMD control involves source control (sealing and covering dumps), chemical treatment (lime neutralization), and biological treatment (constructed wetlands).

DGMS Regulation 131 mandates that mine water discharge must be treated to meet environmental standards.

The objective is to prevent acid generation, neutralize existing acid, and protect ecosystems from contamination.

🧠 4. MCQs (DGMS Exam Format)

1. AMD stands for –

  • A. Acidic Metal Drainage
  • B. Acid Mine Drainage
  • C. Active Mine Dewatering
  • D. Alkaline Mine Discharge
  • E. None
Solution: AMD = Acid Mine Drainage.

2. Primary mineral responsible for AMD –

  • A. Calcite
  • B. Pyrite
  • C. Quartz
  • D. Feldspar
  • E. Dolomite
Solution: Pyrite (FeS₂) oxidation produces acid.

3. Main acid formed in AMD –

  • A. Nitric acid
  • B. Sulphuric acid
  • C. Carbonic acid
  • D. Hydrochloric acid
  • E. Acetic acid
Solution: Sulphuric acid forms due to oxidation of sulphides.

4. AMD water generally has pH –

  • A. 2–4
  • B. 5–7
  • C. 7–9
  • D. 9–11
  • E. 12–14
Solution: AMD water is highly acidic (pH < 4).

5. The oxidation of Fe²⁺ to Fe³⁺ occurs in presence of –

  • A. Nitrogen
  • B. Oxygen
  • C. Carbon dioxide
  • D. Sulphur
  • E. Hydrogen
Solution: Oxygen catalyzes Fe oxidation.

6. Fe(OH)₃ formed during AMD is commonly called –

  • A. Yellow boy
  • B. Green slime
  • C. Red mud
  • D. Iron rust
  • E. Brown ash
Solution: “Yellow boy” is ferric hydroxide precipitate.

7. Biological AMD treatment uses –

  • A. Algae
  • B. Sulphate-reducing bacteria
  • C. Protozoa
  • D. Fungi
  • E. None
Solution: SRB convert sulphates into sulphides.

8. DGMS Regulation related to mine water discharge –

  • A. 128
  • B. 129
  • C. 130
  • D. 131
  • E. 132
Solution: Reg.131 covers discharge norms.

9. pH range of permissible discharge water –

  • A. 4.5–5.5
  • B. 5.5–7.0
  • C. 6.5–8.5
  • D. 8.5–9.5
  • E. 9.5–10.5
Solution: CPCB standard is 6.5–8.5.

10. Limestone neutralization reaction produces –

  • A. CO₂ and Ca²⁺
  • B. H₂O and Na⁺
  • C. H₂S and Fe²⁺
  • D. Cl₂ and Ca²⁺
  • E. SO₃ and Fe³⁺
Solution: CaCO₃ reacts with H⁺ to release CO₂ and Ca²⁺.

11. Major metal leached in AMD –

  • A. Iron
  • B. Gold
  • C. Silver
  • D. Titanium
  • E. Lead
Solution: Fe is commonly released.

12. Passive AMD control structure –

  • A. Lime dosing unit
  • B. Constructed wetland
  • C. Aeration tank
  • D. Filter press
  • E. Thickener
Solution: Wetlands are passive control systems.

13. Heavy metal pollution from AMD causes –

  • A. Corrosion
  • B. Fish kills
  • C. Soil infertility
  • D. All of the above
  • E. None
Solution: AMD leads to multiple effects.

14. AMD formation accelerates in presence of –

  • A. Sunlight
  • B. Thiobacillus ferrooxidans
  • C. Algae
  • D. Moss
  • E. None
Solution: These bacteria catalyze pyrite oxidation.

15. Lime neutralization tank is used to –

  • A. Increase acidity
  • B. Reduce acidity
  • C. Remove metals only
  • D. Filter sediments
  • E. Store water
Solution: Lime raises pH and neutralizes acidity.

16. AMD most commonly occurs in –

  • A. Limestone mines
  • B. Coal & sulphide mines
  • C. Clay mines
  • D. Sandstone quarries
  • E. Salt mines
Solution: Coal and sulphide-rich ores cause AMD.

17. Main oxidizing agent in AMD –

  • A. O₂
  • B. N₂
  • C. CO₂
  • D. H₂S
  • E. NH₃
Solution: Oxygen drives oxidation.

18. Ferric hydroxide precipitate color –

  • A. Blue
  • B. Yellow
  • C. Black
  • D. White
  • E. Pink
Solution: Yellow-brown coloration.

19. Neutralization efficiency depends on –

  • A. Contact time
  • B. Surface area
  • C. pH
  • D. All of the above
  • E. None
Solution: All influence reaction efficiency.

20. Acidic mine water corrodes –

  • A. Concrete
  • B. Steel
  • C. Pumps
  • D. All
  • E. None
Solution: Acid water corrodes all metal parts.

21. AMD is an example of –

  • A. Point-source pollution
  • B. Non-point source
  • C. Air pollution
  • D. Noise
  • E. Thermal
Solution: Mine discharge is point-source.

22. The biological oxidation of Fe²⁺ increases –

  • A. Acidity
  • B. Alkalinity
  • C. Temperature
  • D. pH
  • E. None
Solution: Produces more H⁺ ions.

23. Sulphate-reducing bacteria act in –

  • A. Aerobic condition
  • B. Anaerobic condition
  • C. Both
  • D. Sunlight
  • E. Neutral pH only
Solution: SRB function under anaerobic conditions.

24. AMD prevention priority is –

  • A. Treatment only
  • B. Source control first
  • C. Monitoring only
  • D. None
  • E. Storage
Solution: Source control is primary.

25. The most sustainable AMD control –

  • A. Chemical dosing
  • B. Biological wetland
  • C. Continuous pumping
  • D. Dilution
  • E. None
Solution: Constructed wetlands are sustainable.

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