Carrying Capacity & Data Validity
A population cannot grow forever, sooner or later food, space, water or predators put a ceiling on its numbers. That ceiling is the carrying capacity, and it shifts as conditions change. But everything you conclude about an ecosystem rests on the quality of your data. In this final lesson you learn what sets the ceiling, and how to judge whether ecological data is valid, reliable and accurate enough to trust.
Orient yourself
Make a prediction, scan the goals and the key terms, and see which misconception this lesson is built to fix.
Before You Read
warm-upA few rabbits are released onto an island with plenty of grass. At first their numbers explode, then the growth slows and the population levels off.
Before reading: why does the population stop growing even though no predator or disease arrives? Name two things that could be running out, and predict what would happen to the ceiling if a drought killed half the grass.
Learning Intentions
goalsKnow
- What carrying capacity is and the shape of a logistic growth curve
- Biotic and abiotic factors that set and change carrying capacity
- The meaning of validity, reliability and accuracy
Understand
- Why a population levels off at carrying capacity
- How a change in a factor shifts the carrying capacity up or down
- Why data quality determines how much we can trust a conclusion
Can Do
- Explain how biotic and abiotic factors affect carrying capacity
- Evaluate ecological sampling data for validity, reliability and accuracy
- Judge how far a conclusion about an ecosystem is supported
Scan these before reading
vocabMatch each term to its meaning: use the Key Terms card above.
- Carrying capacity
- Logistic growth
- Validity
- Reliability
- Accuracy
- Whether repeating the measurement gives consistent results
- The largest population an ecosystem can support sustainably over time
- How close a measurement lies to the true value
- Rapid growth that slows and levels off as resources become limiting
- Whether the method actually measures what it claims to measure
Misconceptions To Fix
watch outCarrying Capacity & the Growth Curve
Why every population hits a ceiling
Core Content
Carrying Capacity & the Growth Curve
+5 XPWhy every population hits a ceiling
A population grows quickly while resources are plentiful, but as it becomes crowded, limited resources slow the growth until it levels off at the carrying capacity.
Carrying capacity (K) is the maximum population size of a species that an ecosystem can support sustainably, given its resources. A population typically shows logistic (S-shaped) growth: rapid increase at first, then slowing as resources run short, then a plateau around K, where births roughly balance deaths. The population may oscillate slightly around K rather than holding perfectly steady.
The plateau happens because as numbers rise, individuals compete for finite food, water, space and shelter, and waste, disease and predation increase, so the growth rate falls to zero at K. Without these limits, growth would be exponential and unsustainable.
Text description
- Population (up) against time (across); the dashed line is the carrying capacity K.
- Slow start, then rapid growth, then the curve levels off at K.
Pause, copy the highlighted definition and the shape of the logistic curve into your book before moving on.
The maximum population size an ecosystem can support sustainably is its _____ capacity.
What Changes the Carrying Capacity
Biotic and abiotic factors raise or lower K
What Changes the Carrying Capacity
+5 XPBiotic and abiotic factors raise or lower K
We just saw that K is a ceiling. That raises a question: what sets that ceiling, and why does it move? This card answers it → both biotic and abiotic factors determine K, so changing them shifts it.
Carrying capacity is not fixed, it rises when limiting resources increase and falls when they decrease, whether the factor is living or non-living.
Abiotic factors affecting K: availability of water, light, nutrients, temperature, space and shelter. More rain growing more plant food raises the carrying capacity for herbivores; a drought or fire that destroys food and shelter lowers it. Biotic factors affecting K: food supply (prey or plants), predators, competitors, disease and parasites. More predators or a new competitor lowers a population's carrying capacity; removing a predator or competitor can raise it.
So a change in any limiting factor shifts K: for the island rabbits, a drought that halves the grass lowers the carrying capacity, and the rabbit population must fall to the new lower K (often after a crash); a good season raises K and the population can grow again. To explain carrying capacity in a chosen ecosystem, name the specific limiting factors and state which way each pushes K.
Carrying capacity is set by limiting abiotic factors (water, nutrients, temperature, space, shelter) and biotic factors (food supply, predators, competitors, disease). Increasing a limiting resource raises K; a drought, fire, more predators or a new competitor lowers K. A change in any limiting factor shifts K up or down, and the population adjusts toward the new K.
Pause, copy two abiotic and two biotic factors that change K, and the direction of each, into your book.
The dot point asks for a selected ecosystem, so work one properly. Take the semi-arid rangelands of western New South Wales, the country around Broken Hill and the Darling River, and the red kangaroo (Osphranter rufus) that lives there. Rainfall is low and, more importantly, unpredictable: long dry runs broken by heavy falls. That single feature is what makes this ecosystem such a clear case, because the carrying capacity for kangaroos visibly moves up and down within a single human lifetime instead of sitting still.
The abiotic factor and the chain it runs through. Rainfall does not feed a kangaroo directly. Rain grows pasture, and pasture feeds kangaroos, so kangaroo numbers track pasture biomass, which in turn tracks rainfall with a lag of months. Work by Caughley and colleagues in the western rangelands through the 1970s and 1980s established this chain from long-running aerial surveys (summarised in Caughley, Shepherd and Short, Kangaroos: their ecology and management in the sheep rangelands of Australia, 1987). When the drought of 1982–83 broke the pasture, kangaroo numbers fell heavily and then climbed again over the following wet years: across Australia the surveys recorded a fall of about 24 % in red kangaroos and about 35 % in greys (Caughley, Grigg and Smith, Journal of Wildlife Management, 1985). Nothing changed about the kangaroos; the ceiling moved, and the population followed it down and back up.
The biotic factor, tested by an accident of history. The dingo fence separates country where dingoes are controlled from country where they are not, with similar soils, rainfall and vegetation on both sides, which makes it a continent-scale natural experiment: the thing that differs across the line is the predator. Kangaroo density on the dingo-free side runs much higher than on the dingo side (Caughley and colleagues, Australian Wildlife Research, 1980, which measured densities). Later work on the same fence looked at what that density does to the country, reporting lower ground cover and greater grazing pressure where dingoes are absent (Newsome and colleagues, Rangeland Journal, 2001; Letnic and Koch, 2010). Predation is therefore not a minor adjustment to the ceiling in this ecosystem, it is one of the main things setting it, and the state of the ground cover is the evidence that the higher density sits above what the country sustains rather than being a healthier population.
A second case, where the ceiling was moved deliberately. European rabbits reached plague numbers across southern Australia through the first half of the twentieth century. The release of myxoma virus in 1950 cut the population from something of the order of 600 million to around 100 million, and what followed is the whole idea of this lesson in one data set: the population did not simply return to where it had been. It recovered through the following years and then flattened out around a new, lower carrying capacity, because the virus remained endemic and is still one of the factors setting the ceiling; rabbit haemorrhagic disease virus, released in 1996, lowered it again. Read the shape rather than the numbers: a factor that persists moves K permanently, while a one-off event moves the population and leaves K where it was.
Why this example is worth more than a list of factors. It shows the two kinds of factor doing different jobs. Rainfall, through pasture, sets how high the ceiling can go and moves it year to year. Dingo predation holds the population below that ceiling wherever dingoes are present. So the same ecosystem carries two very different kangaroo densities depending on which factor is operating, and an answer that names rainfall alone, or predators alone, describes only half of it. When you are asked to explain carrying capacity in a selected ecosystem, name the ecosystem, name the specific limiting factors, say which way each pushes K, and say what the evidence for that is.
A drought destroys much of the plant food in an ecosystem. The carrying capacity for the herbivores will most likely:
Apply it: Evaluate the Survey
Work the activity in your own book before you read on. This is the first point where you are on your own.
Activity 1
Evaluate the Survey
Pattern C, Structured evaluation
A student estimated a beetle population using mark-release-recapture but: marked only 5 beetles, took just one recapture sample, used a paint mark that washed off in rain, and sampled only the shadiest corner of the field. For each flaw, state whether it harms validity, reliability or accuracy, and suggest a fix. Then judge how much you would trust their conclusion.
Evaluating Validity, Reliability & Accuracy
Can you trust the conclusion the data leads to?
Evaluating Validity, Reliability & Accuracy
+5 XPCan you trust the conclusion the data leads to?
We just explained what shapes a population. That raises a question: how far can we trust the data behind these conclusions? This card answers it → by evaluating validity, reliability and accuracy.
A conclusion about ecosystem dynamics is only as trustworthy as the data behind it, so you must judge whether the data is valid, reliable and accurate.
Validity, does the method measure what it claims, with the right variables controlled? Sampling only the lushest patch is invalid because it is not representative. Reliability, are the results consistent on repetition? Too few quadrats, one recapture, or a tiny sample give unreliable estimates; repeats and large samples improve it. Accuracy, how close is the measurement to the true value? A mark that washes off, mis-identified species, or a wrongly sized quadrat reduce accuracy.
Note the key distinction: data can be reliable but not accurate (consistently wrong) or accurate but not reliable (right once, by chance). To evaluate, judge all three, identify specific flaws and their effect, suggest improvements, and then state how confident the data lets you be in the conclusion, for example: "Because the sampling was random, repeated and used a reliable mark, the estimate is reasonably valid, reliable and accurate, so the conclusion that the population is declining is well supported." Always end an evaluation with that overall judgement.
Validity = measures the right thing, representative and controlled (not just the lushest patch). Reliability = consistent on repetition (improved by repeats/large samples). Accuracy = close to the true value (good marks, correct ID, right quadrat size). Reliable ≠ accurate. To evaluate, judge all three, name flaws and fixes, then state how far the conclusion is supported.
Add the three definitions, the reliable-≠-accurate point, and a concluding-judgement sentence to your notes before the check below.
Now do the evaluation with numbers in front of you, because that is how it appears in an exam. Two student groups estimate the same daisy population in the same 500 m² plot on the same day. The plot is later counted exhaustively, and the true number is 1850.
| Group | Method | The three estimates they obtained | Mean |
|---|---|---|---|
| Group A | Twelve 1 m² quadrats at random coordinates, repeated three times | 1780, 1920, 1835 | 1845 |
| Group B | Three 1 m² quadrats, all placed in the greenest corner, repeated three times | 3040, 3110, 3075 | 3075 |
Reliability first, because it is the easiest to read off. Group A's three estimates span 140, about 8 % of their mean. Group B's span just 70, about 2 % of theirs. On consistency alone, Group B is the more reliable of the two. That result is the whole point of the example: repeating a method carefully tells you nothing about whether the method is any good.
Accuracy next. Group A's mean of 1845 is within 5 of the true 1850, an error under 0.3 %. Group B's 3075 over-estimates by 1225, an error of about 66 %. Group B is consistently, repeatably wrong, which is exactly what "reliable but not accurate" means.
Validity explains why. Group B chose the greenest corner, so their sample was never capable of representing the plot; the flaw is in the design, and no number of repeats can remove it, which is why their tight spread is so misleading. Group A placed quadrats at random coordinates across the whole plot and took four times as many, so their sample could represent the plot, and it did.
The judgement, which is the marks. Group A's conclusion about this population is well supported: the method is valid, reasonably reliable and accurate to better than 1 %. Group B's conclusion should be rejected, not merely treated with caution, because the error is a bias with a known direction, upward, rather than random scatter that averaging could reduce. Finish every evaluation this way: name the specific flaw, say which of validity, reliability or accuracy it damages, say which way it pushes the result, and then state how much confidence the conclusion deserves.
Carrying capacity can rise or fall when the limiting abiotic or biotic factors change.
Data can be reliable (consistent) yet still inaccurate (consistently wrong).
Sampling only the area where a species is most abundant gives valid, representative data.
See where it lands in the real world
Why this matters: setting limits that hold up
Why this matters: setting limits that hold up
Carrying capacity and data quality together underpin real management decisions, how many kangaroos a reserve can sustain, how big a fish stock is and therefore the safe catch, or whether a threatened population is truly recovering. Because money, livelihoods and species' survival ride on these figures, agencies demand data that is valid, reliable and accurate, and reject conclusions drawn from biased or thin sampling. The evaluation skills you finish Focus Area 3 with are exactly what separate a defensible scientific recommendation from a costly mistake.
Two truths and a lie: two of these follow from the card above about setting limits that hold up. Which one is the lie?
Drive It: Grow a Population to Its Limit
+XP for exploringGrowth slows as the population approaches the carrying capacity K
Use the simulation. As the population gets close to the carrying capacity K, what happens to its growth?
Use the simulation. True or false: a J-shaped (exponential) curve can continue indefinitely in a real habitat.
Explain what is meant by the carrying capacity of an ecosystem, and explain how biotic and abiotic factors together determine it.
Explain means giving cause and effect. The question asks how the factors determine carrying capacity, so each factor must be connected to the limit it imposes rather than simply listed.
5 marks. Define carrying capacity, describe the growth curve that reveals it, then take abiotic and biotic factors in turn, then make the point that it is not a fixed number.
The carrying capacity of an ecosystem, usually written K, is the maximum population size of a species that the environment can sustain indefinitely, given the resources available and the conditions prevailing. It is not the largest number that could ever be present at one moment, but the number that can be maintained without the resource base being degraded.
A population introduced to a new area with abundant resources typically grows slowly at first, then rapidly as numbers and breeding individuals increase, then more slowly as resources become limiting, and finally levels off and fluctuates around a ceiling. This produces the logistic, or S-shaped, growth curve, and the ceiling it approaches is the carrying capacity. The slowing is caused by density-dependent factors: as density rises, competition within the species intensifies, food per individual falls, disease spreads more readily, so birth rates fall and death rates rise until the two balance.
Abiotic factors set the ceiling by determining the quantity of resources available and the conditions organisms must tolerate. Rainfall is the clearest Australian example, and it acts through a chain rather than directly: rain grows pasture, pasture feeds herbivores, so kangaroo numbers track pasture biomass, which tracks rainfall with a lag of months. Temperature, soil nutrients, water availability and space act similarly, each setting a limit on how much living matter the system can support. Because these factors vary, particularly rainfall in the Australian rangelands, the ceiling they set moves.
Biotic factors set the ceiling through interactions with other organisms. Predation removes individuals and can hold a population well below the level its food supply alone would support; competition with other species reduces the share of resources available; and disease and parasitism increase mortality at high density. The dingo fence provides a continental-scale natural experiment for this, because it separates country where dingoes are controlled from country where they are not, with similar soils, rainfall and vegetation on either side, and kangaroo density runs much higher on the dingo-free side. With the abiotic conditions essentially matched, the difference is attributable to the predator.
Carrying capacity is therefore a property of the relationship between a population and its environment at a given time, not a fixed attribute of the place. It rises and falls with rainfall and season, it can be lowered permanently if overgrazing degrades the soil and vegetation, and it can be moved deliberately: the release of myxoma virus in 1950 cut Australia's rabbit population from something of the order of 600 million to around 100 million by introducing a new biotic limiting factor. Treating K as a single fixed number is the commonest error in this topic.
The carrying capacity of an ecosystem, usually written K, is the maximum population size of a species the environment can sustain indefinitely given the resources available and the conditions prevailing; it is not the largest number that could be present at one moment but the number maintainable without degrading the resource base. A population introduced to a new area with abundant resources typically grows slowly at first, then rapidly as numbers and breeding individuals increase, then more slowly as resources become limiting, and finally levels off and fluctuates around a ceiling, producing the logistic or S-shaped growth curve whose ceiling is the carrying capacity. The slowing is caused by density-dependent factors: as density rises, competition within the species intensifies, food per individual falls and disease spreads more readily, so birth rates fall and death rates rise until the two balance. Abiotic factors set the ceiling by determining the quantity of resources available and the conditions that must be tolerated, and they usually act through a chain rather than directly: rain grows pasture, pasture feeds herbivores, so kangaroo numbers track pasture biomass, which tracks rainfall with a lag of months, while temperature, soil nutrients, water and space act similarly, and because these vary, particularly rainfall in the Australian rangelands, the ceiling they set moves. Biotic factors set the ceiling through interactions with other organisms: predation removes individuals and can hold a population well below what its food supply alone would support, competition with other species reduces the available share of resources, and disease and parasitism raise mortality at high density. The dingo fence is a continental-scale natural experiment for this, separating country where dingoes are controlled from country where they are not with similar soils, rainfall and vegetation either side, and kangaroo density runs much higher on the dingo-free side, so with abiotic conditions essentially matched the difference is attributable to the predator. Carrying capacity is therefore a property of the relationship between a population and its environment at a given time rather than a fixed attribute of a place: it rises and falls with rainfall and season, can be lowered permanently if overgrazing degrades soil and vegetation, and can be moved deliberately, as when the release of myxoma virus in 1950 cut Australia's rabbit population from something of the order of 600 million to around 100 million by introducing a new biotic limiting factor.
Two groups estimated the same daisy population in one 500 square metre plot on the same day. Group C used twelve quadrats at random coordinates and repeated the survey three times, obtaining 412, 388 and 400. Group D used three quadrats placed near the path edge where daisies were densest and repeated three times, obtaining 690, 702 and 696. The plot was later counted exhaustively and contained 415 daisies. Evaluate the two surveys.
Evaluate asks for a judgement against criteria. The criteria here are named in the dot point, validity, reliability and accuracy, so use all three and keep them separate, because the whole point of this data is that they disagree.
6 marks. Define the three criteria, work out reliability from the spreads, work out accuracy against the true value, assess validity from the method, then judge each group.
Reliability is the consistency of repeated measurements, judged from the spread of the repeats. Accuracy is how close a result is to the true value. Validity is whether the method actually measures what it claims to measure, which here means whether the sampling design can represent the whole plot. The three are independent, and a result can score well on one and badly on another.
Group C's three estimates are 412, 388 and 400, with a mean of 1200 divided by 3, which is 400, and a spread of 412 minus 388, which is 24, or about 6.0 per cent of the mean. Group D's estimates are 690, 702 and 696, with a mean of 2088 divided by 3, which is 696, and a spread of 702 minus 690, which is 12, or about 1.7 per cent of the mean. On consistency alone, Group D is the more reliable of the two, by roughly a factor of three.
The true number is 415. Group C's mean of 400 is 15 below it, an error of 15 divided by 415, or about 3.6 per cent. Group D's mean of 696 is 281 above it, an error of 281 divided by 415, or about 68 per cent. Group C is accurate to within about 4 per cent, while Group D over-estimates the population by more than two-thirds. Group D is therefore consistently, repeatably wrong, which is exactly what reliable but not accurate means.
Validity explains the accuracy result. Group C placed twelve quadrats at random coordinates, so every part of the plot had an equal chance of being sampled and the mean per quadrat estimates the plot mean: the design is valid for the question asked. Group D placed three quadrats near the path edge where daisies were densest, so the sample was drawn from the densest part of the plot and its mean estimates the density of that patch rather than of the plot. The design is invalid for estimating the whole population, and it fails in a known direction, upward. Group D also used only three quadrats against twelve, so even a valid design would have rested on a much smaller sample.
Group C's survey is valid, reasonably reliable and accurate to within about 4 per cent, so its conclusion about this population is well supported and can be reported, with the spread of 24 quoted as an indication of uncertainty. Group D's survey should be rejected rather than merely treated with caution. Its error is a bias with a known direction, upward, caused by deliberate non-random placement, not random scatter, so averaging more repeats would not reduce it: every additional sample from the same dense patch would be inflated in the same way. Its high reliability is evidence only that the bias is consistent.
Group D could be repaired by placing quadrats at random coordinates across the whole plot, by increasing the number of quadrats substantially, and by reporting the spread of its repeats alongside the mean. The general lesson is that reliability is measurable from your own data while accuracy is not, because the true value is almost never known in the field, so validity is what must be judged before any estimate is trusted. A consistent result from a biased design is the most dangerous outcome in ecological sampling, because it looks like good data.
Reliability is the consistency of repeated measurements, judged from the spread of the repeats; accuracy is closeness to the true value; and validity is whether the method measures what it claims, which here means whether the design can represent the whole plot. The three are independent, and this data shows them disagreeing. On reliability, Group C's estimates of 412, 388 and 400 give a mean of 1200 divided by 3, or 400, with a spread of 24, about 6.0 per cent of the mean, while Group D's estimates of 690, 702 and 696 give a mean of 2088 divided by 3, or 696, with a spread of 12, about 1.7 per cent of the mean, so on consistency alone Group D is the more reliable by roughly a factor of three. On accuracy, against a true value of 415, Group C's mean of 400 is 15 below, an error of about 3.6 per cent, while Group D's mean of 696 is 281 above, an error of about 68 per cent; Group D is consistently and repeatably wrong, which is precisely what reliable but not accurate means. Validity explains that result. Group C placed twelve quadrats at random coordinates so every part of the plot had an equal chance of being sampled and the mean per quadrat estimates the plot mean, making the design valid for the question asked, whereas Group D placed three quadrats near the path edge where daisies were densest, so its sample estimates the density of that patch rather than of the plot, making the design invalid and failing in a known direction, upward; Group D also used three quadrats against twelve, so even a valid design would have rested on a far smaller sample. Group C's survey is therefore valid, reasonably reliable and accurate to within about 4 per cent, so its conclusion is well supported and can be reported with the spread of 24 quoted as an indication of uncertainty. Group D's should be rejected rather than merely treated with caution, because its error is a bias with a known direction caused by deliberate non-random placement rather than random scatter, so averaging further repeats would not reduce it, every additional sample from the same dense patch being inflated identically, and its high reliability is evidence only that the bias is consistent. It could be repaired by random placement across the whole plot, substantially more quadrats, and reporting the spread alongside the mean. The general lesson is that reliability is measurable from your own data while accuracy usually is not, since the true value is rarely known in the field, so validity must be judged before any estimate is trusted: a consistent result from a biased design is the most dangerous outcome in ecological sampling, because it looks like good data.
Practise independently
Answer every question in your own words first. The model answers are for checking against, not for copying.
Multiple Choice
+5 XPA fresh set drawn from this lesson's question bank, feedback shown immediately. +5 XP per correct · +25 XP all correct
Pick your answer, then rate your confidence, that tells the system what to drill next.
Short Answer, 15 marks
+5 XPEvaluateBand 6(7 marks) 1. Explain how biotic and abiotic factors affect the carrying capacity of an ecosystem, and evaluate how the validity, reliability and accuracy of sampling data affect the conclusions that can be drawn about population changes.
1 mark: carrying capacity defined · 2 marks: an abiotic and a biotic factor each shown to shift K with direction · 3 marks: validity, reliability and accuracy each correctly explained in a sampling context · 1 mark: overall judgement linking data quality to confidence in the conclusion
ApplyBand 4(4 marks) 2. A population of possums in a reserve has been stable for several years. A fire then destroys most of the hollow-bearing trees they nest in, while the food plants recover within a season. Explain what happens to the carrying capacity and to the population, and identify whether the limiting factor involved is biotic or abiotic.
1 mark: identifies tree hollows as shelter or nesting sites, an abiotic resource provided by a biotic structure, and accepts either classification if justified · 1 mark: states that the carrying capacity falls because a required resource has been reduced · 1 mark: states that the population must fall toward the new lower K, and that the fall may lag behind the fire · 1 mark: notes that K does not recover with the food plants, because hollows take decades to form, so the ceiling stays low long after the vegetation looks recovered
EvaluateBand 5-6(4 marks) 3. Two groups estimate the same plant population. Group A takes twelve random quadrats three times and gets 1780, 1920 and 1835. Group B takes three quadrats in the lushest corner three times and gets 3040, 3110 and 3075. The true population is 1850. Evaluate the two data sets and justify which conclusion you would accept.
1 mark: identifies Group B as the more consistent, and therefore more reliable on spread alone · 1 mark: identifies Group A as far more accurate, within about 0.3 % of the true value against Group B over-estimating by about 66 % · 1 mark: attributes Group B failure to validity, a non-representative sample chosen by eye, and states that repeats cannot fix a design flaw · 1 mark: reaches a judgement, accepting Group A conclusion and rejecting rather than merely qualifying Group B, because the error is a directional bias not random scatter
Show all answers
Multiple choice
MC answers and full explanations are shown inline as you complete each question. Use the retry button to attempt a fresh set from the lesson bank.
Short Answer Model Answer
Q1 (7 marks): Carrying capacity (K) is the maximum population size of a species an ecosystem can support sustainably given its resources. It is set, and shifted, by both abiotic and biotic factors. An abiotic example: the availability of water and food plants, in a drought, plant food and water decline, so K falls and the population must drop toward the new lower ceiling (often after a crash); a good rainfall season raises K and allows growth. A biotic example: predators, competitors and disease, an increase in predators or the arrival of a new competitor lowers a population's K, while removing a predator or competitor can raise it. So a change in any limiting factor moves K up or down, and the population adjusts toward it. Evaluating the data: any conclusion about how a population is changing is only as trustworthy as the sampling data behind it. Validity means the method measures what it claims and is representative, sampling only the densest patch is invalid, so quadrats must be placed randomly and variables controlled. Reliability means consistent results on repetition, too few quadrats or a single mark-recapture sample is unreliable, so taking many samples and repeating improves it. Accuracy means closeness to the true value, a mark that washes off, mis-identified species or a wrongly sized quadrat reduce accuracy. Importantly, data can be reliable yet inaccurate (consistently wrong), so all three must be satisfied. Overall, a conclusion such as "this population is declining" is well supported only when the sampling is valid (random, representative), reliable (repeated, large samples) and accurate (correct methods and identification); if the data is biased or thin, the conclusion should be treated with caution.
Q2 (4 marks): The limiting resource here is shelter, specifically the tree hollows the possums nest in. Hollows are part of the living vegetation but function as physical nesting space, so either classification is defensible provided it is justified: the hollow itself is a non-living structure, while its supply depends on living trees [1]. Because a required resource has been sharply reduced, the carrying capacity of the reserve for possums falls: the ecosystem can now support fewer possums sustainably than it could before the fire [1]. The population must therefore fall toward the new, lower ceiling, through a combination of deaths and animals failing to breed or dispersing in search of nest sites, and the fall may lag behind the fire itself rather than happening the moment the trees burn [1]. The important point is the timing of any recovery. The food plants regrow within a season, so it is tempting to say K recovers with them, but it does not: hollows form only in old trees over many decades, so the ceiling stays low long after the reserve looks green and recovered. This is why shelter, not food, is the limiting factor in this ecosystem after fire, and why nest boxes are used as a management response [1].
Q3 (4 marks): Taken on consistency alone, Group B looks better. Their three estimates span only 70, about 2 % of their mean of 3075, while Group A's span 140, about 8 % of their mean of 1845, so Group B is the more reliable of the two in the strict sense of giving repeatable results [1]. Accuracy reverses the picture completely. Against the true value of 1850, Group A's mean of 1845 is out by 5, an error of about 0.3 %, while Group B's 3075 over-estimates by 1225, an error of about 66 %. Group B is consistently and substantially wrong, which is the textbook case of data that is reliable but not accurate [1]. The reason lies in validity. Group B chose their quadrat positions by eye, in the lushest corner, so their sample was never capable of representing the whole plot; the flaw is in the design rather than the execution, and this is exactly why their tight spread is dangerous, repeating a biased method faithfully reproduces the bias and makes the result look trustworthy. Group A placed quadrats at random coordinates across the plot and took four times as many, so their sample could represent the population, and the closeness to the true value shows that it did [1]. My judgement is that I would accept Group A's conclusion, which rests on a valid, reasonably reliable and highly accurate estimate, and I would reject Group B's rather than merely treat it with caution. The distinction matters: random scatter can be reduced by averaging more samples, but Group B's error is a bias with a known direction, upward, so collecting more data the same way would make the wrong answer more precise without making it any less wrong [1].
Retrieve and reflect
Do the spaced-review set from memory first, then look back at the prediction you made before you read anything.
Check what actually stuck
A short spaced-review set drawn from this lesson and the lessons before it. Answer from memory first, that is what makes it stick.
Lock it in
bossYou can now explain how biotic and abiotic factors set and shift carrying capacity, and evaluate ecological data for validity, reliability and accuracy. That completes Focus Area 3, Evolution and ecosystems. You have travelled from natural selection and adaptation all the way to the dynamics and measurement of whole ecosystems.
↩ Back to focus-area hubHow did your thinking change?
You explained why the island rabbits levelled off. As their numbers rose, limited resources, food (grass), water, space and shelter, began to run out, so competition increased and the growth rate fell to zero at the carrying capacity. This is logistic, S-shaped growth. If a drought killed half the grass, the carrying capacity would fall, because a key limiting resource is reduced, and the rabbit population would have to drop toward the new, lower ceiling.
The deeper lesson of the whole focus area is that every such conclusion depends on data, and you should always ask whether that data is valid, reliable and accurate before trusting what it tells you about an ecosystem.