Environmental Biology IV: Toxicology and Microbiology — Absorption, Distribution, Biotransformation and Excretion, Acute and Chronic Toxicity, Bioassay, TLV, Margin of Safety and Therapeutic Index, Water-Borne Diseases and Airborne Microbes — and Environmental Biotechnology: Bioremediation, Bioindicators, Biofertilisers, Biofuels and Biosensors
2. Acute and chronic toxicity, bioassay, TLV, margin of safety and therapeutic index
Acute toxicity results from a single dose or a short exposure, usually within 24 to 96 hours, and is measured by the median lethal dose (LD₅₀, the dose in mg per kg of body weight that kills half the test animals) or, for exposure through water or air, the median lethal concentration (LC₅₀). The lower the LD₅₀, the more toxic the substance. Chronic toxicity results from repeated exposure to lower doses over a long period, a large part of the lifespan, and shows as cancer, organ damage, reproductive and developmental effects or neurotoxicity; it is characterised by the no-observed-adverse-effect level (NOAEL) and the lowest-observed-adverse-effect level (LOAEL). The dose-response curve for most toxic effects is S-shaped with a threshold below which no effect is seen; for genotoxic carcinogens regulators generally assume no threshold, so that any dose carries some risk. Two toxicants together may act additively, synergistically (asbestos and smoking multiply the risk of lung cancer) or antagonistically.
A bioassay measures the effect of a substance or effluent on living organisms under standard conditions, and it captures the combined toxicity of a mixture that chemical analysis of single substances cannot. Standard aquatic bioassays include the 96-hour fish LC₅₀, the 48-hour Daphnia immobilisation test and algal growth inhibition; the luminescence of the bacterium Vibrio fischeri gives a rapid screening test. A "safe" concentration for continuous exposure is often estimated by multiplying the 96-hour LC₅₀ by an application factor, commonly between 0.01 and 0.1.
| Measure | Definition | Interpretation |
|---|---|---|
| Threshold limit value, time-weighted average (TLV-TWA) | The average airborne concentration to which nearly all workers may be exposed for an 8-hour day and 40-hour week, day after day, without adverse effect (set by the ACGIH) | An occupational, not an ambient, standard |
| TLV-STEL and TLV-C | Short-term exposure limit, a 15-minute average not to be exceeded; ceiling, a concentration never to be exceeded even briefly | Protect against acute effects of peaks |
| Therapeutic index | TD₅₀ ÷ ED₅₀ (or LD₅₀ ÷ ED₅₀): median toxic or lethal dose divided by median effective dose | The larger it is, the safer the substance |
| Margin of safety | LD₁ ÷ ED₉₉: the dose lethal to 1% divided by the dose effective in 99% | More conservative than the therapeutic index because it compares the tails of the two curves |
A worked case: if a pesticide used as an antiparasitic in livestock has an LD₅₀ of 400 mg/kg and an ED₅₀ of 20 mg/kg, its therapeutic index is 400 ÷ 20 = 20. Two substances with the same therapeutic index can differ in margin of safety if one has a much steeper dose-response curve. In environmental risk assessment the term margin of safety (or margin of exposure) is also used for the NOAEL divided by the estimated human exposure, where a large ratio means the exposure is well below the level at which effects begin.
3. Major water-borne diseases and airborne microbes
| Pathogen group | Disease and agent | Note |
|---|---|---|
| Bacteria | Cholera (Vibrio cholerae), typhoid (Salmonella Typhi), bacillary dysentery (Shigella), diarrhoea from pathogenic Escherichia coli | Transmitted by the faecal-oral route; controlled by safe water, sanitation and chlorination |
| Viruses | Hepatitis A and E, poliomyelitis, rotavirus diarrhoea | Hepatitis E causes large water-borne outbreaks in India and is especially dangerous in pregnancy |
| Protozoa | Amoebic dysentery (Entamoeba histolytica), giardiasis (Giardia), cryptosporidiosis (Cryptosporidium) | Cysts and oocysts resist chlorine; Cryptosporidium is removed mainly by filtration |
| Helminths | Guinea-worm disease (Dracunculus medinensis), ascariasis | India was certified free of guinea-worm disease by the WHO in 2000 |
Because pathogens are many and scarce, water is tested instead for indicator organisms that are always present in faeces in large numbers and survive about as long as pathogens: total coliforms, faecal (thermotolerant) coliforms and above all Escherichia coli, whose presence proves faecal contamination. Airborne microbes, or bioaerosols, include bacteria such as Mycobacterium tuberculosis and Legionella pneumophila, which grows in cooling towers and hot-water systems and causes Legionnaires' disease; viruses such as influenza, measles and SARS-CoV-2, spread by droplets and fine aerosols; and fungal spores of Aspergillus, Penicillium, Alternaria and Cladosporium, which cause allergies and asthma and, in people with weakened immunity, infection. Crowded, poorly ventilated and damp buildings concentrate them. They are sampled with impactors such as the Andersen sampler, which sorts particles by size onto culture plates.
4. Bioremediation: in situ and ex situ, by microbes and plants
Bioremediation is the use of living organisms, chiefly microbes and plants, to degrade, transform, remove or immobilise pollutants in soil, water or sediment. Microbes mineralise organic pollutants to carbon dioxide and water or transform metals to less toxic or less mobile forms. Among the best-known agents are Pseudomonas species, including the oil-degrading strain for which Ananda Chakrabarty obtained the first patent on a genetically engineered organism after Diamond v. Chakrabarty (United States Supreme Court, 1980); the white-rot fungus Phanerochaete chrysosporium, whose lignin-degrading peroxidases also break down PAHs, dyes and chlorinated compounds; and Deinococcus radiodurans, which tolerates intense radiation. In India a bacterial consortium developed by TERI, marketed as Oilzapper, has been used to clean oil-contaminated soils and sludges.
| Approach | Techniques | Principle |
|---|---|---|
| In situ (treated in place) | Biostimulation, bioaugmentation, bioventing, biosparging, monitored natural attenuation | Supply oxygen, nutrients or microbes to the contaminated zone without excavation; cheaper and less disruptive but slower and harder to control |
| Ex situ (excavated or pumped out) | Landfarming, biopiles, composting, slurry-phase bioreactors, pump-and-treat with bioreactors | Treat the material under controlled conditions; faster and more certain but costly |
Phytoremediation uses plants. Phytoextraction takes metals up into the shoots, which are harvested; hyperaccumulators such as Noccaea (formerly Thlaspi) caerulescens for zinc and cadmium, Indian mustard (Brassica juncea) for lead and the Chinese brake fern Pteris vittata for arsenic are the models. Phytostabilisation immobilises metals in the root zone to stop erosion and leaching; phytodegradation and rhizodegradation break down organics within plants or through microbes in the rhizosphere; rhizofiltration absorbs contaminants from water onto roots, as sunflowers did for radionuclides in ponds near Chernobyl; and phytovolatilisation releases selenium or mercury to the air in volatile form, which moves rather than removes the problem.
5. Bioindicators, biofertilisers, biofuels and biosensors
| Tool | Examples | Environmental use |
|---|---|---|
| Bioindicators | Lichens, which disappear near sources of SO₂ (the "lichen desert" of cities); mayfly, stonefly and caddisfly larvae in clean streams; Tubifex worms and red chironomid larvae in organically polluted water; E. coli for faecal contamination | Integrate pollution over time; biotic indices score a stream by which groups survive |
| Biofertilisers | Rhizobium in legume nodules; free-living Azotobacter and associative Azospirillum; cyanobacteria and the Azolla-Anabaena symbiosis in rice fields; phosphate-solubilising bacteria such as Bacillus megaterium; arbuscular mycorrhizal fungi such as Glomus | Supply nitrogen and phosphorus biologically, reducing chemical fertiliser use and its runoff |
| Biofuels | First generation: ethanol from sugarcane molasses and grain, biodiesel from vegetable oils; second generation: cellulosic ethanol from crop residues; third generation: algal oils; biogas | Replace fossil fuels; first-generation fuels compete with food crops for land, which later generations avoid |
| Biosensors | A biological recognition element (enzyme, antibody, nucleic acid or whole cell) coupled to a transducer (electrochemical, optical or piezoelectric) | Rapid field detection: acetylcholinesterase sensors for organophosphate and carbamate pesticides, microbial BOD sensors, luminescent bacterial sensors for toxicity |
Key takeaways
- Toxicants are absorbed through the lungs, gut and skin, stored in fat, bone or kidney, biotransformed by phase I (P450) and phase II (conjugation) reactions, sometimes into more toxic forms, and excreted mainly in urine and bile.
- Acute toxicity is measured by LD₅₀ or LC₅₀ and chronic toxicity by NOAEL and LOAEL; bioassays capture the toxicity of whole effluents.
- The TLV-TWA is an occupational 8-hour, 40-hour-week limit; the therapeutic index is TD₅₀ (or LD₅₀) ÷ ED₅₀ and the margin of safety LD₁ ÷ ED₉₉.
- Cholera, typhoid, hepatitis A and E, amoebiasis, giardiasis and cryptosporidiosis are water-borne and traced by E. coli as the indicator; Legionella, tuberculosis, influenza and fungal spores are airborne.
- Bioremediation is in situ (biostimulation, bioaugmentation, bioventing, biosparging) or ex situ (landfarming, biopiles, bioreactors); phytoremediation uses hyperaccumulators such as Pteris vittata for arsenic; bioindicators, biofertilisers, biofuels and biosensors complete the toolkit.
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.
A veterinary antiparasitic compound has an LD₅₀ of 400 mg/kg and an ED₅₀ of 20 mg/kg in the target animal. What is its therapeutic index?
Numerical answer — type the value.
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Answer: 20
Therapeutic index = LD₅₀ ÷ ED₅₀ = 400 ÷ 20 = 20; the larger the index, the wider the gap between the effective and the lethal dose. Dividing the ED₅₀ by the LD₅₀ (0.05) inverts the ratio.The TLV-TWA of a chemical is the average airborne concentration to which
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Answer: C — nearly all workers may be exposed for an 8-hour day and a 40-hour week without adverse effects
The TWA is an occupational limit for a normal working day and week. A lifetime limit for the public is an ambient standard, a concentration killing half the animals is the LC₅₀, and the 15-minute limit is the short-term exposure limit (STEL).Cholera is caused by
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Answer: B — the bacterium Vibrio cholerae
Cholera is a bacterial disease of Vibrio cholerae spread through faecally contaminated water, causing profuse watery diarrhoea. Entamoeba causes amoebic dysentery, hepatitis E virus causes jaundice, and Salmonella Typhi causes typhoid.Which of the following are phase II biotransformation reactions? Select all that apply.
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Answer: A — Conjugation with sulphate; B — Conjugation with glucuronic acid; C — Conjugation with glutathione
Phase II reactions attach a polar group to the molecule, making it water-soluble for excretion: glucuronide, sulphate and glutathione conjugation are the main ones. Hydroxylation by cytochrome P450 is a phase I oxidation that usually prepares the molecule for conjugation.Which plant is a well-known hyperaccumulator used in the phytoextraction of arsenic?
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Answer: C — The Chinese brake fern, Pteris vittata
Pteris vittata can accumulate arsenic in its fronds at concentrations thousands of times those in soil and is the standard arsenic hyperaccumulator. Sunflowers were used in rhizofiltration of radionuclides, and water hyacinth absorbs many pollutants from water but is not the arsenic model.Assertion (A): Outbreaks of cryptosporidiosis can occur even from properly chlorinated drinking water. Reason (R): Cryptosporidium oocysts are highly resistant to chlorine at the doses used in water treatment. Choose the correct option.
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Answer: A — Both A and R are true, and R is the correct explanation of A
Both are true and R explains A. Because chlorine at normal doses does not inactivate the oocysts, removal depends on effective coagulation and filtration or on ultraviolet disinfection; the Milwaukee outbreak of 1993, which sickened hundreds of thousands, followed a failure of filtration.In toxicology, the margin of safety of a substance is defined as
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Answer: A — the dose lethal to 1% of the population divided by the dose effective in 99% (LD₁ ÷ ED₉₉)
The margin of safety compares the lowest lethal tail with the highest effective tail of the two dose-response curves, LD₁ ÷ ED₉₉, which makes it stricter than the therapeutic index, LD₅₀ ÷ ED₅₀. The inverted ratio and the NOAEL-LOAEL gap are not the definition.Which of the following are in situ bioremediation techniques? Select all that apply.
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Answer: A — Biosparging; C — Bioventing
Bioventing supplies air to unsaturated soil and biosparging injects air below the water table, both treating contamination where it lies. Landfarming and biopiles first excavate the soil and treat it elsewhere, which makes them ex situ methods.Which organisms are most widely used as bioindicators of sulphur dioxide pollution in air?
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Answer: C — Lichens
Lichens absorb water and gases over their whole surface and have no protective cuticle, so they are highly sensitive to SO₂ and disappear near sources, leaving "lichen deserts" in polluted cities. Tubifex indicates organic pollution of water and coliforms faecal contamination.A pesticide is present in lake water at 0.002 mg/L, and fish from the lake contain 5 mg/kg of it. What is the bioconcentration factor in L/kg?
Numerical answer — type the value.
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Answer: 2500
BCF = concentration in organism ÷ concentration in water = 5 mg/kg ÷ 0.002 mg/L = 2,500 L/kg. A high BCF marks a fat-soluble, persistent chemical; dividing the water concentration by the fish concentration gives 0.0004, the inverse.