Question 5 of 6: Contaminants of Concern and Mine Water

Question 5: Contaminants of Concern and Mine Water (20 marks)

Question text not reproduced: the examination questions are © Engineers and Geoscientists BC. Open the official past paper (linked at the top of this page) to read the question, then follow the worked solution below.

A. Contaminants of concern (8 marks)

Arsenic. Arsenic occurs naturally in sulfide minerals commonly associated with base and precious metal deposits (notably arsenopyrite, FeAsS), and is mobilized into mine water alongside iron and sulfate during the same oxidative weathering that generates acid rock drainage from waste rock and tailings (Question 3). It is a recognized human carcinogen, and chronic low-level exposure via contaminated drinking water causes skin lesions and internal cancers; it is also acutely toxic to aquatic organisms. Its transport and fate are strongly pH- and redox-dependent – arsenic tends to adsorb onto iron oxyhydroxide precipitates under near-neutral, oxidizing conditions (limiting mobility) but is released again under either very low pH or reducing (low-oxygen) conditions, making it persistently mobile at many mine-impacted sites.

Mercury. Inorganic mercury reaches mine sites both as a trace natural constituent of some ore bodies and, historically, from gold amalgamation processing (a legacy contamination source at many older gold mines and downstream placer-mining areas). Organic mercury (methylmercury) is not usually released directly by mining; instead it forms when inorganic mercury deposited in anoxic sediments or wetlands downstream of a mine site is methylated by sulfate-reducing bacteria. Methylmercury bioaccumulates and biomagnifies strongly up the aquatic food chain, so fish consumption is the dominant human exposure pathway (a particular concern for Indigenous communities relying on country foods); it is a potent neurotoxin, with developing fetuses and young children most sensitive to its effects.

B. Mine water treatment (12 marks)

i) Three mine water control technologies (6 marks):

• Diversion ditches/channels – intercept and route clean upgradient surface water around the disturbed mine area; objective is to minimize the volume of water that ever contacts mine facilities and therefore needs treatment.
• Groundwater interception (pumping wells or cutoff walls) – capture contaminated groundwater before it can reach a receiving watercourse; objective is to route captured water to treatment rather than allow uncontrolled seepage discharge.
• Engineered covers and liners on waste rock and tailings facilities – reduce infiltration of precipitation into reactive material; objective is to reduce both the water-rock contact time and the total contaminant loading generated at the source, reducing the volume and concentration of water needing subsequent treatment.

ii) Active vs. passive treatment (6 marks): Active treatment (e.g. a lime neutralization/high-density-sludge plant) uses continuous mechanical and chemical processes – requiring ongoing energy input, reagent supply and trained operating staff – to achieve rapid, tightly controlled water quality regardless of influent variability; it produces a sludge by-product requiring ongoing disposal, has the highest operating cost of the two approaches, and still requires effluent monitoring to demonstrate compliance. Passive treatment (e.g. a constructed wetland, anoxic limestone drain, or sulfate-reducing bioreactor) relies on gravity flow and natural biological/geochemical processes with minimal energy or labour input, giving much lower long-term operating cost and making it well suited to closed/legacy sites where an operator will not remain indefinitely; it requires a larger land footprint, responds more slowly to changing influent conditions, and still requires periodic performance monitoring (it is not "walk away and forget"), but needs far less active maintenance than a mechanical plant.