The effect of industrial pollution on groundwater quality
An analysis of how industrial organic pollutants affect groundwater quality, aquatic microflora and the salinity of surface waters.
Industrial pollution reaches groundwater through infiltration from the surface, leaking underground installations and landfills. The groups most often detected are petroleum substances, chlorinated solvents, heavy metals and salts. Detection requires piezometer monitoring, because in groundwater contamination travels for years, invisible from the surface.
Groundwater has one property that sets it apart from every other part of the environment: it responds late, and for a long time gives no signal at the surface. Contamination that entered the ground years ago may be crossing the property boundary right now — and nobody will notice without measurement.
How pollutants get in
- Infiltration from the surface — leaks, spills, poor storage of substances, run-off from manoeuvring and loading areas.
- Leaking underground installations — tanks, pipelines and separators whose condition is hard to assess without testing.
- Landfills and waste storage — leachate passing through permeable layers.
- Industrial wastewater — discharged contrary to permit or with a composition different from the one declared.
What we find most often
Samples of water and soil are analysed primarily for petroleum substances and heavy metals — mercury, lead, cadmium, zinc and arsenic. Added to these are chlorinated solvents, typical of metalworking plants and dry cleaners, and salinity, characteristic of mining and chemical industries.
Each group behaves differently in the ground. Petroleum substances, lighter than water, accumulate on the water table; chlorinated solvents, heavier, sink to the base of the aquifer. That distinction determines the depth at which a sample must be taken — which is why sampling points cannot be chosen at random.
Effects on the aquatic environment
Organic pollutants reduce dissolved oxygen, which directly affects the aquatic microflora responsible for natural self-purification. Heavy metals accumulate in organisms and bottom sediments, from which they can be released for years after emissions have stopped. Salinity changes the species composition of aquatic communities, including in surface waters fed by groundwater.
How it is detected
The basis is a network of piezometers placed with regard to the direction of groundwater flow, always with points upgradient and downgradient of the potential source. Samples are taken cyclically, to capture a trend rather than a single reading.
It is worth remembering that a local groundwater monitoring network is not mandatory equipment for every industrial facility — its scope follows from specific administrative decisions and can often be optimised. See environmental monitoring. Analyses are carried out with an accredited laboratory, because only such results carry evidential weight.
Frequently asked questions
Through monitoring from piezometers placed upgradient and downgradient of the potential source, following the direction of flow. Samples are taken cyclically and analysed in an accredited laboratory — a single measurement will not show a trend.
It depends on the substance and the geology. Petroleum substances degrade microbially over years; heavy metals effectively do not disappear — they accumulate in soil and sediment and can be released long after emissions cease.
Usually not. Oily substances on water or a change in soil colour are sometimes visible, but in most cases the only way to confirm it is laboratory analysis of samples taken from the right depth.
Need a quote for testing or remediation?
Describe the site and the planned investment — we will prepare a free quote and advise which scope of testing the regulations require.