Ink LearningBiologyPracticalsExam boards

BiologyEcology, populations and environmental change › Nitrogen, phosphorus and the trouble with fertiliser

Nitrogen, phosphorus and the trouble with fertiliser

Energy passes through an ecosystem once and leaves as heat. Atoms do not: the same nitrogen has been in and out of living things many times, and four groups of bacteria do the moving. Get those four straight — which one starts in the air, which one needs oxygen, which one destroys the supply — and the rest of this topic, eutrophication included, follows from them.

Before this Proteins and the amino acid · Nucleotides and ATP · Aerobic respiration and the electron transport chain · Gross and net primary productivity

Before you start

Eutrophication kills fish because the algae are toxic. Some blooms genuinely are — certain cyanobacteria release toxins that can kill a dog that drinks from the water — which is why the idea survives. But it is not the mechanism a mark scheme wants, and it is not what usually kills the fish. The fish suffocate. The algae die and bacteria decompose them, and those bacteria respire aerobically in enormous numbers, stripping the dissolved oxygen out of the water. The killer is several steps removed from the bloom, and every one of those steps is a marking point.

What you should be able to do

Why nitrogen is worth four bacteria

Nitrogen is in every amino acid, so it is in every protein and every enzyme; in every nucleotide, so it is in DNA, RNA, ATP, NAD and NADP; and in the ring at the centre of chlorophyll. A plant short of nitrogen shows it as stunted growth and yellowing older leaves.

Nitrogen is also the commonest gas in the air, at about 78 per cent, and almost nothing can touch it: the two atoms in N2 are held by a triple bond that takes a great deal of energy to break, and no plant or animal can do it. So a plant standing in an atmosphere four fifths made of the element it is short of takes its nitrogen from the soil instead, as nitrate ions absorbed by active transport into the root hairs, and to a lesser extent as ammonium. Four groups of prokaryotes fill that gap, and they are the reason a soil holds nitrate at all.

Four processes, and how to stop muddling them

More marks are lost here than anywhere else in ecology, and almost always to the same slip: writing 'nitrification' where the answer is 'nitrogen fixation'. The words look alike and the processes have nothing in common. Fixation starts with a gas; nitrification starts with something already dissolved in the soil.

Read it left to right and the nitrogen is being oxidised at every step: gas, then ammonium, then nitrite, then nitrate. Only the first arrow and the long one along the bottom touch the atmosphere, and they run in opposite directions.

Nitrogen fixation. Nitrogen gas is reduced to ammonia, which picks up a hydrogen ion in the soil to become ammonium. The enzyme, nitrogenase, is destroyed by oxygen, and that shapes where fixation happens. Rhizobium lives inside nodules on the roots of legumes — peas, beans, clover — in a mutualistic relationship: the plant supplies carbohydrate and a protein, leghaemoglobin, that mops up oxygen, and the bacterium supplies fixed nitrogen. Free-living fixers include Azotobacter in soil and cyanobacteria in water and flooded rice fields. Lightning fixes a little, and the Haber process fixes an industrial quantity.

Ammonification. Saprobiotic bacteria and fungi break down the nitrogen-containing compounds in dead organisms, faeces and urine, releasing ammonium into the soil: proteins are hydrolysed to amino acids and deaminated, urea is hydrolysed by urease. Nothing here comes from the air — ammonification returns nitrogen that was already in the ecosystem.

Nitrification. Two oxidations, one after the other, carried out by two different genera. Nitrosomonas oxidises ammonium to nitrite; Nitrobacter oxidises nitrite to nitrate. Both are chemoautotrophs — they use the energy released by these oxidations to fix carbon dioxide — and both need oxygen, because oxygen is what they are oxidising with. Nitrification is the process that produces the ion plants actually take up in quantity.

Denitrification. In soil with no oxygen in it, certain bacteria such as Pseudomonas respire using nitrate as the final electron acceptor in place of oxygen. The nitrogen ends up as nitrogen gas and leaves the soil. This is the only one of the four that takes nitrogen out of the ecosystem, and the only one that requires oxygen to be absent.

ProcessStarts withEnds withCarried out byOxygen
Nitrogen fixationNitrogen gas from the airAmmoniumRhizobium in root nodules; free-living Azotobacter; cyanobacteriaNitrogenase is destroyed by it, so fixation happens where oxygen is kept away
AmmonificationProtein, urea and other nitrogen compounds in dead matter and wasteAmmoniumSaprobiotic bacteria and fungiFaster when aerobic
NitrificationAmmonium, then nitriteNitrite, then nitrateNitrosomonas, then NitrobacterRequired: these are oxidations
DenitrificationNitrateNitrogen gasDenitrifying bacteria such as PseudomonasRequired to be absent: nitrate is used instead of oxygen

Three hooks keep the four apart under pressure. Fix means fasten: fixation fastens nitrogen from the air onto hydrogen, and it is the only way in. Nitrification has 'nitrite' and 'nitrate' inside the word, and both its start and its finish are already in the soil. De-nitrification undoes the lot and is the only way out.

The oxygen column explains three things a farmer does. Ploughing and draining keep the soil aerated, favouring nitrification and suppressing denitrification, so nitrate builds up; compacted or waterlogged soil does the reverse and loses nitrogen as gas; and planting clover or beans in a rotation brings Rhizobium with them, adding fixed nitrogen without a bag of fertiliser.

TRY IT — Reading a soil experiment

A soil sample is divided into three. Sample A is left well-drained and aerated. Sample B is flooded and sealed so that no oxygen can reach it. Sample C is heated to 120 °C for twenty minutes and then cooled. Ammonium sulfate solution is added to all three and the nitrate concentration is measured over two weeks. Nitrate rises steadily in A, falls to nearly zero in B and does not change in C. Explain all three results.

Check your answer

In A the soil is aerated, so Nitrosomonas and Nitrobacter can carry out nitrification: the added ammonium is oxidised to nitrite and then to nitrate, and the nitrate concentration rises. Both steps are oxidations and both need oxygen, which is available.

In B there is no oxygen, so nitrification cannot proceed and no nitrate is made from the added ammonium. Any nitrate already present is used by denitrifying bacteria as an alternative electron acceptor in respiration, so it is reduced to nitrogen gas and the concentration falls towards zero.

In C the heating has killed the bacteria, and nitrification is a biological process, so nothing oxidises the ammonium and the nitrate concentration does not change. Sample C is the control that shows the changes in A and B were caused by organisms rather than by chemistry — and saying what the sterile sample is for is the mark most often dropped here.

The decomposers, and the fungi that trade with roots

Ammonification is done by saprobionts: organisms that feed on dead material by secreting enzymes onto it, digesting it outside themselves and absorbing the products. That extracellular digestion is why a rotting log has a soft wet zone around the fungus rather than a bite taken out of it, and without it every atom of nitrogen would end up locked in corpses.

Mycorrhizae are a different arrangement and a commonly confused one. A mycorrhiza is a mutualistic association between a fungus and a plant root: the fungal hyphae are far finer than root hairs and spread through a much larger volume of soil, greatly increasing the surface area available for absorbing water and mineral ions — phosphate especially, which moves through soil very slowly. In return the fungus receives organic compounds the plant has made by photosynthesis. Mycorrhizae are named explicitly in AQA 7402's nutrient cycles content, and a plant with them typically takes up phosphate several times faster than one without.

Saprobiont
An organism that obtains its energy from dead material by secreting enzymes onto it and absorbing the soluble products.
Mycorrhiza
A mutualistic association between a fungus and a plant root, in which the fungus increases the surface area for absorbing water and mineral ions and receives organic compounds in return.

Phosphorus: the cycle with no gas in it

Phosphorus is in the phosphate groups of ATP, in the backbone of DNA and RNA, and in every phospholipid in every membrane. Plants take it up as phosphate ions from the soil solution, and animals get it by eating plants.

Compare the shape of this with the nitrogen cycle. There is no box for the atmosphere, no bacterium turning phosphate into a gas and none turning it back, and the only return from the sea takes geological time.

The structural difference from nitrogen is that no stage of the phosphorus cycle is gaseous. Phosphate has no volatile form under ordinary conditions, so the atmosphere plays no part, and the reservoir is rock rather than air. Phosphate is released from rock by weathering, dissolves in the soil solution, is taken into plants, passes into animals, and is returned to the soil by decomposers acting on dead material, urine and faeces.

That has two consequences examiners like. The cycle is slow: the geological return, from sediment on the sea bed back to rock through uplift, takes millions of years, so phosphate washed into the ocean is lost from the land on any human timescale, and rock phosphate mined for fertiliser is a finite deposit. And phosphate is often the limiting nutrient in fresh water and on old, heavily weathered soils, precisely because there is no atmospheric source to top it up.

Bacteria matter here too, in one role rather than four: they decompose organic phosphorus compounds and release phosphate back into the soil. Mycorrhizal fungi then do much of the work of getting it into roots.

One board difference is worth knowing. AQA 7402 names the phosphorus cycle and expects the role of microorganisms in it; OCR A H420 builds its recycling content round carbon and nitrogen; Cambridge 9700's A-level ecology leans towards ecosystems, niche and the measurement of biodiversity. Find out which you are sitting before deciding how much of this section to memorise.

Fertiliser, leaching and what happens downstream

Every harvest removes nitrogen and phosphorus from a field in the crop. In a natural ecosystem the dead plant would rot where it fell and the nutrients would return; agriculture breaks that loop on purpose and has to close it artificially.

Natural fertilisers — manure, slurry, compost, sewage sludge — are organic matter, so their nitrogen is locked in protein and must be ammonified and then nitrified before a plant can use it. It becomes available slowly, over weeks, and the organic matter improves soil structure. The drawbacks are bulk and unknown composition. Artificial fertilisers are inorganic salts of known composition, whose nitrate is immediately available to the crop — which is the point of them — and immediately available to the next rainstorm, which is the problem with them.

Leaching is what follows. Nitrate ions are very soluble and carry a negative charge, and clay particles and humus in soil also carry a net negative charge, so nitrate is not held and washes down through the soil with the rain into groundwater and streams. Ammonium, being positive, is held far more strongly, which is one reason it leaches less. Phosphate is much less soluble and travels mainly attached to eroded soil particles rather than in solution, so it reaches watercourses mostly when bare soil is washed off a field.

How much nitrogen, and how much of it leaves

A farmer spreads ammonium nitrate, NH4NO3, at 250 kg per hectare over a 12-hectare field. Take the relative formula mass of ammonium nitrate as 80 and the relative atomic mass of nitrogen as 14. Calculate the mass of nitrogen applied. If 30 per cent of it is leached into a stream that carries 5.0 × 107 litres of water over the same period, calculate the concentration of nitrogen in the stream in milligrams per litre.

First the percentage of nitrogen in the fertiliser. There are two nitrogen atoms in NH4NO3, so 2 × 14 = 28 out of 80, which is 28 ÷ 80 = 0.35, or 35 per cent.

Nitrogen applied per hectare is 250 × 0.35 = 87.5 kg, and over 12 hectares that is 87.5 × 12 = 1 050 kg of nitrogen.

Thirty per cent of that is leached: 1 050 × 0.30 = 315 kg, which is 315 000 g, or 3.15 × 108 mg.

Divide by the volume: 3.15 × 108 ÷ 5.0 × 107 = 6.3 mg of nitrogen per litre. Expressed as nitrate rather than as nitrogen this is 6.3 × (62 ÷ 14) = 28 mg of nitrate per litre, since the relative formula mass of the nitrate ion is 62.

Now the judgement the question is after. That is below the 50 mg per litre limit set for nitrate in drinking water, but it is more than twenty times the concentration of an unpolluted upland stream and far more than enough to relieve the shortage that was holding the algae back. A figure can be legally safe to drink and ecologically disastrous at once.

Watch the units. Nitrate is quoted either as milligrams of nitrate per litre or as milligrams of nitrogen per litre, and the two differ by a factor of 4.4.

Eutrophication, one consequence at a time

Eutrophication means nutrient enrichment of a body of water. It happens naturally over centuries as lakes silt up; fertiliser runoff and treated sewage compress that into a season. Running the chain in order is the difference between a two-mark answer and a six-mark one.

Watch the oxygen bar in particular. It does not move when the bloom appears, and it does not move when the plants die. It collapses only when the bacteria arrive, which is the step everybody leaves out.

One. Nitrate leaches off the land into the water, or phosphate arrives with eroded soil and treated sewage. In fresh water the nutrient in shortest supply is usually phosphate; in estuaries and coastal water it is usually nitrogen. Either way, the factor limiting the algae has just been relieved.

Two. Algae and cyanobacteria at the surface multiply rapidly — an algal bloom — because they already had light, carbon dioxide and warmth and now have the nutrient too.

Three. The bloom forms a dense mat and blocks the light. Submerged rooted plants and deeper algae are shaded, so photosynthesis falls below respiration and they die.

Four. Those dead plants, and the bloom itself once it exhausts the nutrient and dies back, are a vast supply of dead organic matter. Saprobiotic bacteria feed on it and their population grows enormously.

Five. Those bacteria respire aerobically, and this is the step that does the killing: they take dissolved oxygen out of the water faster than it can dissolve back in from the air, so the biochemical oxygen demand rises sharply and the dissolved oxygen concentration falls.

Six. Fish and invertebrates needing well-oxygenated water suffocate. Trout, mayfly and stonefly nymphs go first; tolerant bloodworms and Tubifex worms survive and may become abundant, which is why stream invertebrates are used as indicator species. If the oxygen falls far enough, anaerobic bacteria take over and the water smells of hydrogen sulfide.

Two refinements are worth carrying into an exam. The algae themselves photosynthesise and release oxygen by day, so the bloom is not the thing removing it; the depletion is worst at night and worst of all once the bloom dies. And a fish kill is usually reported as sudden, because dissolved oxygen can fall past a lethal threshold in hours after weeks of nothing visible happening.

The remedies follow the chain rather than the symptom: buffer strips of uncultivated land between field and watercourse; fertiliser applied in spring onto a growing crop rather than in autumn onto bare soil; soil tested first so that only what the crop needs is applied; and phosphate stripped at sewage works, since phosphate is usually the limiting nutrient in fresh water.

In the exam

Check yourself

A river is sampled at four points below a farm. Point 1 is upstream of the farm; point 2 is immediately below a field drain; point 3 is two kilometres downstream; point 4 is ten kilometres downstream. Nitrate concentration is 2, 34, 30 and 11 mg per litre at the four points, and dissolved oxygen is 9.8, 9.4, 3.1 and 7.6 mg per litre. Explain the two patterns and explain why the lowest oxygen is not found at the point with the most nitrate.

Answer

Nitrate is low upstream because the water has not yet passed the farm. It jumps at point 2 because nitrate has leached from the fertilised field — nitrate ions are very soluble and are not held by negatively charged soil particles, so rain washes them through into the drain — and falls downstream as the river is diluted and as algae and plants absorb it.

Dissolved oxygen is barely affected at point 2 even though the nitrate is at its highest there. That is the key observation: nitrate does not remove oxygen, and nor do the algae, which photosynthesise and release it. Nothing has yet happened that consumes oxygen.

By point 3 the enriched water has had time for the sequence to run. The algal bloom that the nitrate allowed has multiplied, matted over the surface and blocked light from the plants below, which have died; the bloom itself has begun to die back. Saprobiotic bacteria are decomposing all of that dead material and have multiplied enormously, and their aerobic respiration is taking dissolved oxygen out of the water faster than it can dissolve in. Hence the minimum at 3.1 mg per litre.

By point 4 most of the dead material has been decomposed, the bacterial population has fallen back and the oxygen demand with it, so oxygen dissolves in again from the air and the concentration recovers. The distance between cause and effect is the point of the question: each step takes time, so the damage appears downstream of where the nutrient entered, and the farm responsible for a fish kill is often well upstream of the dead fish.

Questions

Written to the command words the boards use. Try them on paper before opening a scheme: the marks go to points made, not to length.

Question 15 marks

Describe the sequence of events by which nitrate leaching from a fertilised field leads to the death of fish in a lake.

Mark scheme
  1. B1 nitrate ions are very soluble and are not held by the negatively charged clay and humus particles, so rain washes them down through the soil into the water, relieving the shortage of the nutrient that was limiting the algae
  2. B1 algae and cyanobacteria at the surface multiply rapidly to form an algal bloom, because they already had light, carbon dioxide and warmth and now have the nutrient too
  3. B1 the bloom forms a dense mat that blocks the light, so submerged rooted plants and deeper algae photosynthesise below the rate at which they respire, and die
  4. B1 those dead plants, and the bloom itself once it exhausts the nutrient and dies back, are a vast supply of dead organic matter on which saprobiotic bacteria feed, so the bacterial population grows enormously
  5. B1 those bacteria respire aerobically and take dissolved oxygen out of the water faster than it can dissolve back in from the air, so the dissolved oxygen concentration falls and fish and invertebrates needing well-oxygenated water suffocate

Question 24 marks

Compare nitrogen fixation with nitrification, referring to what each starts with, what each produces, the organisms responsible and the part oxygen plays.

Mark scheme
  1. B1 fixation starts with nitrogen gas from the atmosphere, whereas nitrification starts with ammonium already present in the soil, so only fixation brings nitrogen into the ecosystem
  2. B1 fixation reduces nitrogen gas to ammonia, which takes up a hydrogen ion to become ammonium, whereas nitrification oxidises ammonium to nitrite and then nitrite to nitrate
  3. B1 fixation is carried out by Rhizobium in the root nodules of legumes, by free-living soil bacteria such as Azotobacter and by cyanobacteria, whereas nitrification is carried out by Nitrosomonas and then Nitrobacter
  4. B1 nitrogenase is destroyed by oxygen, so fixation happens where oxygen is kept away and leghaemoglobin mops it up inside a nodule, whereas nitrification requires oxygen because both of its steps are oxidations

Question 34 marks

Explain why a well-drained, ploughed soil holds more nitrate than a compacted, waterlogged one.

Mark scheme
  1. B1 ploughing and draining keep air in the spaces between the soil particles, so oxygen is available
  2. B1 nitrification is carried out by Nitrosomonas and Nitrobacter and both of its steps are oxidations requiring oxygen, so ammonium is oxidised through nitrite to nitrate and nitrate accumulates
  3. B1 in a compacted or waterlogged soil the spaces are filled with water and oxygen is absent, so nitrification stops and no further nitrate is produced
  4. B1 denitrifying bacteria such as Pseudomonas then respire using nitrate as the final electron acceptor in place of oxygen, converting it to nitrogen gas that leaves the soil, so the nitrate already there is lost as well

Question 44 marks

A 25-hectare field receives ammonium nitrate, NH4NO3, at 200 kg per hectare; take its relative formula mass as 80 and the relative atomic mass of nitrogen as 14. Over the following months a stream draining the field carries 8.0 × 107 litres of water, and its nitrogen concentration is on average 5.6 mg per litre higher than upstream of the field. Calculate the mass of nitrogen applied and calculate what percentage of it reached the stream.

Mark scheme
  1. M1 there are two nitrogen atoms in NH4NO3, so nitrogen is 2 × 14 = 28 of the relative formula mass of 80, which is 28 ÷ 80 = 0.35, or 35 per cent by mass
  2. A1 nitrogen applied = 200 × 0.35 = 70 kg per hectare, and over 25 hectares that is 1750 kg
  3. M1 nitrogen carried by the stream = 5.6 × 8.0 × 107 = 4.48 × 108 mg, which is 448 kg
  4. A1 448 ÷ 1750 = 0.256, so about 25.6 per cent of the nitrogen applied reached the stream

Question 53 marks

Phosphate is usually the nutrient in shortest supply in fresh water, and the phosphorus cycle has no gaseous stage. Suggest why stripping phosphate from effluent at a sewage works reduces algal blooms in the river below it, and suggest why phosphate carried out to sea is not replaced on any useful timescale.

Mark scheme
  1. B1 the algae are limited by whichever nutrient is in shortest supply, so removing phosphate leaves that shortage in place and the bloom cannot develop even where other nutrients are plentiful
  2. B1 sewage effluent is a continuous point source of phosphate, so treating it at the works removes the input rather than treating the symptom, and one works serves a whole town
  3. B1 phosphate has no volatile form, so there is no atmospheric route back to the land; the return from sea-bed sediment to rock by uplift and weathering takes millions of years, so on any human timescale the phosphate is lost

Question 62 marks

Name the genus of bacteria that oxidises ammonium to nitrite, and name the genus that oxidises nitrite to nitrate.

Mark scheme
  1. B1 Nitrosomonas oxidises ammonium to nitrite
  2. B1 Nitrobacter oxidises nitrite to nitrate

Worth remembering

← Populations and their limits: what stops the numbers rising · Succession: how bare rock becomes woodland, and why we stop it →