Environmental Pollution and Control IV: Soil Pollution — Soil Properties and Quality Analysis, Industrial Effluents and Soil, Soil Micro-Organisms and the Degradation of Pesticides and Fertilisers, and Control — and Thermal Pollution and Heat Islands, Marine Pollution, its Abatement and Coastal Management, and Radioactive Pollution, Radiation Standards and Protection

This chapter completes Unit VI with its last two items. For soil it covers the physico-chemical and biological properties relevant to pollution, the analysis of soil quality, the interaction of industrial effluents with soil components, soil micro-organisms and their role in degrading pesticides and synthetic fertilisers, and soil pollution control, with the sodium adsorption ratio worked. It then takes thermal pollution and urban heat islands; the sources and impacts of marine pollution, the methods of abating it and coastal management; and radioactive pollution: its sources, the biological effects of ionising radiation, the units of exposure and dose, radiation standards and radiation protection, with an equivalent dose and the inverse-square law worked. Soil formation and properties were taught in Unit IV, and the law of the coast is taught in Unit VIII.

1. Soil properties and the analysis of soil quality

The properties that govern how soil holds and releases pollutants are texture (clay soils bind far more than sandy ones), structure and porosity (which control infiltration and leaching), pH (most metals are more mobile in acid soils), cation exchange capacity, organic matter (which binds metals and organic chemicals) and redox status. The biological properties, microbial biomass, soil respiration and enzyme activities such as dehydrogenase, are sensitive early indicators of pollution because microbes respond before crops do. Soil quality is analysed from composite samples, many sub-samples from a field mixed together, usually from 0 to 15 cm for agricultural soils.

Soil testStandard method
pH and electrical conductivityElectrode in a 1:2 or 1:2.5 soil-water suspension; conductivity of the extract for salinity
Organic carbonWalkley-Black wet oxidation with potassium dichromate and sulphuric acid
Available nitrogenAlkaline permanganate method (Subbiah and Asija)
Available phosphorusOlsen's sodium bicarbonate extraction for neutral and alkaline soils; Bray's extraction for acid soils
Available potassiumNeutral ammonium acetate extraction and flame photometry
Micronutrients and heavy metalsDTPA extraction (Lindsay and Norvell) for available zinc, copper, iron and manganese; acid digestion and AAS or ICP for total metals

India's Soil Health Card scheme, launched in 2015, tests farm soils for twelve parameters, including the major and micronutrients, pH, EC and organic carbon, and gives crop-wise fertiliser recommendations, both to raise yields and to curb the overuse of fertilisers.

2. Industrial effluents and soil, soil micro-organisms, and soil pollution control

When industrial effluents are used for irrigation or discharged on land, their constituents interact with soil components by adsorption on clays, humus and oxides, precipitation, complexation and redox reactions. Tannery effluents, rich in chromium and salts, have left chromium-contaminated soils and groundwater in leather clusters such as those around Vellore in Tamil Nadu and Kanpur in Uttar Pradesh. Distillery spent wash is very high in BOD, potassium and dark colour; textile effluents carry dyes and salts; and effluents high in sodium disperse clays, destroying soil structure and permeability. Sodicity is assessed by the sodium adsorption ratio, SAR = Na⁺ ÷ √[(Ca²⁺ + Mg²⁺) ÷ 2], with concentrations in milliequivalents per litre: water with 20 meq/L of sodium, 3 of calcium and 5 of magnesium has SAR = 20 ÷ √4 = 10. Soils with an exchangeable sodium percentage above about 15 are sodic. Other sources of soil pollution are mining and smelting, excessive agrochemicals (pesticide residues and cadmium from phosphate fertilisers), municipal solid waste and sewage sludge, e-waste recycling, oil spills and plastics.

Soil micro-organisms, bacteria, actinomycetes (which produce many antibiotics and the earthy smell of geosmin), fungi, algae and protozoa, decompose organic matter, cycle nutrients, form soil aggregates and degrade pollutants. Pesticides are degraded when microbes use them as a source of carbon or energy, or by co-metabolism, in which an enzyme made for another substrate transforms the pesticide incidentally: Pseudomonas and other bacteria degrade 2,4-D, Flavobacterium hydrolyses parathion, and Pseudomonas sp. ADP mineralises atrazine. Persistence depends on chemical structure, halogenated and highly branched molecules being resistant, which is why DDT can persist for years while organophosphates break down in weeks; the idea that for every natural compound some microbe can degrade it, Alexander's principle of microbial infallibility, fails for many synthetic, recalcitrant chemicals. Synthetic fertilisers are transformed microbially too: urea is hydrolysed by urease to ammonia, which can volatilise; ammonium is nitrified to mobile nitrate, which leaches; and nitrate is denitrified to nitrogen and nitrous oxide.

Soil pollution is controlled first at the source, by treating effluents before land application, integrated pest and nutrient management, and safe disposal of waste. Contaminated land is remediated by excavation and secure disposal, soil washing, stabilisation and solidification (binding contaminants with cement or lime), thermal desorption, and biological methods, bioremediation and phytoremediation. Amendments reduce the availability of contaminants: liming acid soils raises pH and immobilises most metals, organic matter binds metals and pesticides, and gypsum reclaims sodic soils by replacing exchangeable sodium with calcium, which is then leached away.

3. Thermal pollution and heat islands

Thermal pollution is the degradation of water quality by a change in its temperature, above all the discharge of heated cooling water from thermal and nuclear power stations using once-through cooling, and from steel mills, refineries and other industries. Warm water holds less dissolved oxygen, while it raises the metabolic rate and oxygen demand of fish and invertebrates, so it squeezes them from both sides; it can cause thermal shock and fish kills, disrupt spawning and migration timed by temperature, favour heat-tolerant and invasive species and algal blooms, and increase the toxicity of many pollutants. Sudden cooling when a plant shuts down can be as harmful. It is controlled by closed-cycle cooling with natural- or mechanical-draft cooling towers, cooling ponds and spray ponds, and by recovering waste heat. Under Indian rules, the temperature of cooling water discharged from once-through systems must not exceed that of the receiving water by more than 5 °C, and new thermal power plants have been required to adopt closed-cycle cooling.

An urban heat island is a city that is markedly warmer than its rural surroundings, the difference being greatest on calm, clear nights. Its causes are dark, dry surfaces of asphalt and roofing that absorb sunlight (low albedo) and store heat; the replacement of vegetation and soil, which cool by evapotranspiration, with impervious surfaces; street canyons that trap radiation and reduce wind; waste heat from vehicles, air conditioners and industry; and polluted air that traps outgoing radiation. Its consequences are heat stress and deaths during heat waves, especially among outdoor workers, the poor and the elderly; higher electricity demand for cooling, which adds emissions; faster formation of ozone; and changes in local rainfall. Mitigation uses cool (reflective) roofs and pavements, green roofs, trees and parks, water bodies and better urban design. Ahmedabad's Heat Action Plan (2013), the first in South Asia, combined early warning with public health measures and has been widely copied in Indian cities.

4. Marine pollution, its abatement, and coastal management

Most marine pollution, about four-fifths by common estimate, comes from the land: sewage, agricultural runoff, industrial discharges and the plastics carried by rivers. Nutrient runoff creates coastal "dead zones" of hypoxic water, the best known in the Gulf of Mexico off the Mississippi, and fuels harmful algal blooms and red tides that poison shellfish. Oil enters the sea from tanker accidents such as the Exxon Valdez (1989) and from well blowouts such as Deepwater Horizon (2010), but more from routine operational discharges, runoff and natural seeps; it smothers seabirds and mammals, destroying the insulation of feathers and fur, and coats shorelines and mangroves. Plastics and microplastics entangle and are ingested by turtles, seabirds and fish; mercury and persistent organic pollutants biomagnify to high levels in top predators such as tuna; ships' ballast water transports invasive species; and warming and acidification bleach corals.

Instrument or methodPurpose
MARPOL 73/78The main international convention on pollution from ships: oil, noxious liquids, harmful packaged goods, sewage, garbage (including a ban on discharging plastics) and air emissions
London Convention (1972) and its 1996 ProtocolControl the dumping of wastes at sea
UN Convention on the Law of the Sea (1982)Obliges states to protect and preserve the marine environment and sets jurisdictional zones
Ballast Water Management Convention (2004, in force 2017)Requires ships to manage ballast water to stop the spread of invasive organisms
Oil spill responseContainment booms and skimmers, sorbents, chemical dispersants, in situ burning and bioremediation with nutrients
Land-based controlSewage treatment, reduced fertiliser runoff, industrial effluent control and plastic waste management

Coastal management aims to balance development with the protection of ecosystems and communities along the coast. Integrated coastal zone management treats the coast as one system of land, estuary and sea and brings the many agencies and users together; in India a World Bank-supported integrated coastal zone management project began in Gujarat, Odisha and West Bengal around 2010, and the Coastal Regulation Zone notifications regulate activities along the shore. Practical measures include protecting and restoring mangroves, coral reefs, seagrass and dunes, which buffer storms and tsunamis; preferring "soft" engineering such as beach nourishment to hard sea walls that shift erosion elsewhere; setback lines for construction; and hazard mapping for cyclones, storm surges and sea-level rise.

5. Radioactive pollution: sources, biological effects, exposure, standards and protection

Most of the radiation dose people receive is natural: cosmic rays, terrestrial radionuclides of the uranium and thorium series and potassium-40 in rocks, soil and building materials, radionuclides in food and water, and above all inhaled radon and its decay products, which contribute roughly half of the natural dose. The worldwide average natural background is about 2.4 mSv a year, higher in places such as the monazite-sand coast of Kerala. The largest human-made source is medical: diagnostic X-rays, CT scans and nuclear medicine. Smaller contributions come from fallout from past atmospheric weapons tests, the nuclear fuel cycle from mining to waste, industrial radiography and accidents such as Chernobyl (1986) and Fukushima Daiichi (2011).

Ionising radiation damages living cells by breaking chemical bonds in DNA directly and, more often, indirectly through free radicals formed when it splits water molecules. By the law of Bergonié and Tribondeau (1906), cells that divide rapidly and are less differentiated, such as those of bone marrow, the gut lining, gonads and the fetus, are the most radiosensitive. Effects are of two kinds. Deterministic effects (tissue reactions) occur only above a threshold dose and grow more severe with dose: skin burns, cataracts, sterility and acute radiation syndrome, which appears after whole-body doses above about 1 Gy. Stochastic effects, cancer and heritable effects, are assumed to have no threshold, their probability, not their severity, rising with dose; this linear no-threshold assumption underlies radiation protection.

QuantityUnitMeaning
ActivityBecquerel (Bq), one disintegration per second; the older curie equals 3.7 × 10¹⁰ BqHow radioactive a source is
Absorbed doseGray (Gy), one joule absorbed per kilogram; 1 Gy = 100 radEnergy deposited in tissue
Equivalent doseSievert (Sv) = absorbed dose × radiation weighting factor (1 for gamma rays, X-rays and beta particles; 20 for alpha particles; energy-dependent for neutrons)Biological harm to an organ, allowing for the type of radiation
Effective doseSievert, the sum of equivalent doses to each tissue weighted by its sensitivityOverall risk to the whole person, the quantity used in dose limits

An absorbed dose of 2 mGy from alpha particles is an equivalent dose of 2 × 20 = 40 mSv, the same energy doing twenty times the biological harm of gamma rays. The International Commission on Radiological Protection recommends dose limits of 1 mSv a year effective dose for members of the public from planned sources, over and above natural background and medical exposure, and 20 mSv a year for radiation workers, averaged over five years with no more than 50 mSv in any one year. In India the Atomic Energy Regulatory Board, set up in 1983, enforces these limits. Radiation protection rests on three principles, justification, optimisation (keeping doses as low as reasonably achievable, ALARA) and dose limitation, and on three practical controls: minimising the time of exposure, maximising distance, since dose rate from a point source falls with the square of distance (40 µSv/h at 1 m becomes 10 µSv/h at 2 m), and shielding, lead or concrete for gamma rays, a few millimetres of aluminium or plastic for beta particles, and paper or skin for alpha particles, which are dangerous mainly when inhaled or swallowed.

Key takeaways

  • Soil texture, pH, CEC, organic matter and redox govern pollutant retention; soil quality is analysed by Walkley-Black carbon, alkaline permanganate nitrogen, Olsen's or Bray's phosphorus, ammonium acetate potassium and DTPA micronutrients.
  • Tannery effluents leave chromium in soils; SAR = Na ÷ √[(Ca + Mg) ÷ 2] measures sodicity; microbes degrade pesticides directly or by co-metabolism, while halogenated compounds such as DDT persist; gypsum reclaims sodic soils.
  • Thermal discharges lower dissolved oxygen while raising oxygen demand, controlled by cooling towers and a 5 °C discharge limit; urban heat islands come from low albedo, lost vegetation and waste heat, and are eased by cool roofs, trees and heat action plans.
  • About four-fifths of marine pollution is land-based; MARPOL, the London Convention, UNCLOS and the Ballast Water Convention govern the sea; integrated coastal zone management and the protection of mangroves and reefs guard the coast.
  • Radon gives about half the natural dose of about 2.4 mSv a year; deterministic effects have thresholds and stochastic effects are assumed to have none; Sv = Gy × weighting factor (alpha 20); ICRP limits are 1 mSv (public) and 20 mSv (workers) a year; time, distance and shielding protect.

Practice questions (10)

Attempt each one before opening the answer. Every explanation names the tempting wrong option as well as the right one, because that is where marks are lost.

  1. An irrigation water contains 20 meq/L of sodium, 3 meq/L of calcium and 5 meq/L of magnesium. What is its sodium adsorption ratio?

    Numerical answer — type the value.

    Show answer

    Answer: 10

    SAR = Na ÷ √[(Ca + Mg) ÷ 2] = 20 ÷ √[(3 + 5) ÷ 2] = 20 ÷ √4 = 20 ÷ 2 = 10. Dividing by (Ca + Mg) without taking the square root of half their sum gives 2.5, which would badly understate the sodium hazard.
  2. A worker's lung tissue receives an absorbed dose of 2 mGy from alpha particles. Taking the radiation weighting factor of alpha particles as 20, what is the equivalent dose in mSv?

    Numerical answer — type the value.

    Show answer

    Answer: 40

    Equivalent dose = absorbed dose × radiation weighting factor = 2 mGy × 20 = 40 mSv. Gray measures energy per kilogram; the sievert allows for the much greater biological damage done by densely ionising alpha particles, so the equal-energy gamma dose would be only 2 mSv.
  3. Organic carbon in soil is most commonly determined in the laboratory by

    1. the alkaline permanganate method
    2. DTPA extraction
    3. the Walkley-Black wet oxidation method with potassium dichromate
    4. Olsen's sodium bicarbonate extraction
    Show answer

    Answer: C — the Walkley-Black wet oxidation method with potassium dichromate

    Walkley-Black oxidises soil organic carbon with dichromate in sulphuric acid and back-titrates the excess. Olsen's method extracts available phosphorus, DTPA available micronutrients and the alkaline permanganate method available nitrogen.
  4. Which of the following are effects of thermal pollution on aquatic ecosystems? Select all that apply.

    1. Disruption of spawning cycles timed by temperature
    2. A rise in the metabolic rate and oxygen demand of fish
    3. A fall in dissolved oxygen
    4. An increase in the solubility of oxygen
    Show answer

    Answer: A — Disruption of spawning cycles timed by temperature; B — A rise in the metabolic rate and oxygen demand of fish; C — A fall in dissolved oxygen

    Warm water holds less oxygen while making organisms need more, and many life cycles are cued by temperature, so heated discharges stress aquatic life in several ways at once. Oxygen solubility falls, not rises, as temperature increases.
  5. The urban heat island effect is usually most intense

    1. on calm, clear nights, when rural areas cool quickly but the city releases stored heat slowly
    2. during heavy monsoon rain
    3. only in winter at high latitudes
    4. at noon on cloudy, windy days
    Show answer

    Answer: A — on calm, clear nights, when rural areas cool quickly but the city releases stored heat slowly

    Concrete and asphalt store heat by day and release it at night, and urban canyons reduce radiative cooling, so the city-rural difference peaks on still, clear nights. Wind and cloud mix and even out temperatures, weakening the effect.
  6. Assertion (A): Gypsum is applied to reclaim sodic soils. Reason (R): Calcium from gypsum replaces exchangeable sodium on the clay, and the displaced sodium is leached away. Choose the correct option.

    1. Both A and R are true, and R is the correct explanation of A
    2. Both A and R are true, but R is not the correct explanation of A
    3. A is true, but R is false
    4. A is false, but R is true
    Show answer

    Answer: A — Both A and R are true, and R is the correct explanation of A

    Both are true and R explains A. Exchangeable sodium disperses clay and destroys structure; calcium sulphate supplies calcium that displaces the sodium, which then leaves in drainage water as sodium sulphate, so the soil flocculates and regains permeability.
  7. MARPOL 73/78 is the main international convention on

    1. persistent organic pollutants
    2. the protection of wetlands
    3. the prevention of pollution from ships
    4. transboundary movements of hazardous wastes
    Show answer

    Answer: C — the prevention of pollution from ships

    MARPOL covers oil, noxious liquids, packaged goods, sewage, garbage and air emissions from ships. Transboundary hazardous waste is the Basel Convention, wetlands the Ramsar Convention and persistent organic pollutants the Stockholm Convention.
  8. Which statements about the biological effects of ionising radiation are correct? Select all that apply.

    1. Alpha particles are harmless because paper stops them
    2. Deterministic effects such as cataracts occur only above a threshold dose
    3. Rapidly dividing cells such as those of bone marrow are especially radiosensitive
    4. The severity of a radiation-induced cancer increases with dose
    Show answer

    Answer: B — Deterministic effects such as cataracts occur only above a threshold dose; C — Rapidly dividing cells such as those of bone marrow are especially radiosensitive

    Deterministic effects have thresholds, and by the law of Bergonié and Tribondeau dividing, undifferentiated cells are most sensitive. For stochastic effects like cancer it is the probability, not the severity, that rises with dose; and alpha emitters are very dangerous inside the body, as inhaled radon shows, even though they cannot penetrate skin.
  9. The dose rate 1 m from a small gamma source is 40 µSv/h. Ignoring absorption in air, the dose rate at 2 m is

    1. 40 µSv/h
    2. 20 µSv/h
    3. 5 µSv/h
    4. 10 µSv/h
    Show answer

    Answer: D — 10 µSv/h

    For a point source dose rate falls with the square of distance, so doubling the distance divides it by four: 40 ÷ 4 = 10 µSv/h. Halving it (20 µSv/h) assumes a linear fall, which applies to neither points nor lines of radiation; distance is one of the three basic protections along with time and shielding.
  10. Under the recommendations of the International Commission on Radiological Protection, the annual effective dose limit for members of the public from planned sources, excluding natural background and medical exposure, is

    1. 1 mSv
    2. 2.4 mSv
    3. 20 mSv
    4. 50 mSv
    Show answer

    Answer: A — 1 mSv

    The public limit is 1 mSv a year. Twenty mSv a year averaged over five years is the occupational limit, 50 mSv the maximum for a worker in any single year, and 2.4 mSv the average natural background, not a limit.