Biology · Earth, Origins & the History of Life
Life on land, mass extinctions and changing ecosystems
A land surface offers a different physical setting from a body of water. Later, a major environmental disruption can change which lineages persist and how they interact. Both transitions require us to follow more than a single rising count of 'advanced' organisms.
Energy, Enzymes & Metabolism supplies electron donors and acceptors, photosynthesis and material/energy accounts. Phylogeny, Classification & the Tree of Life supplies ancestry and evidence comparisons; its methods are not repeated here. Species, Speciation & Macroevolution helps with origin/loss counts, while Development, Differentiation & Stem Cells helps with cell specialisation. The chapter introduces its own dating notation and numerical rules. You can follow the qualitative history first and return to the arithmetic models afterward.
Back to the Biology mapBy the end, you can
Connect environmental constraints with life on land, then distinguish extinction, surviving lineages, later diversity and ecosystem structure.
Moving into air changes several requirements
A photosynthetic surface exposed to air can exchange gases readily, but it can also lose water. Support, protection of developing stages and movement of reproductive cells pose further constraints. Different lineages and environments offer different solutions. Living on land does not mean that an organism no longer needs water.
Fossils place limits on historical claims. Wellman and colleagues described Ordovician plant fragments from Oman containing spores, supporting an interpretation of early land-plant remains. Such evidence concerns particular preserved structures. It does not date the first organism ever to occupy land or prove that all modern land-plant features arose together.
The leaf model examines one present-day kind of physical trade-off: changing the opening of stomata, pores that permit gas exchange. It describes two reversible states of a stomata-bearing leaf, not a population evolving new pores and not the anatomy of every land plant. More opening increases both the assigned potential carbon-dioxide admission and the assigned water loss.
A reversible leaf state changes two consequences
Read the diagram in words
Both states start with eight water units and receive three, giving eleven before loss. The more-open state loses six, ending at five, and has gas-admission index eight. The more-closed state loses two, ending at nine, and has gas-admission index three. The gas indices are compared on their own scale.
| Item | Starting water | Incoming water | Available water | Water loss | Ending water |
|---|---|---|---|---|---|
| More-open state | 8 | 3 | 11 | 6 | 5 |
| More-closed state | 8 | 3 | 11 | 2 | 9 |
| Item | Potential carbon-dioxide admission index |
|---|---|
| More-open state | 8 |
| More-closed state | 3 |
Water units and gas-index units are different
Potential gas admission, not measured carbon fixation
Two assigned reversible surface states of a stomata-bearing leaf under the same conditions. Water and carbon-dioxide indices use different units. Initial water inventory eight; input three per interval; demands are small enough for the supplied inventory. Lower opening decreases both assigned loss and potential gas admission. No realised carbon fixation, growth, fitness, ancestral anatomy or inherited population change is measured.
A present mechanism is not a complete origin story
Cuticles, gas-exchange arrangements and ways of protecting reproductive stages can be studied as mechanisms. Establishing when particular arrangements evolved requires historical evidence in addition to understanding what they do now. A leaf responding within an afternoon and a lineage changing over generations are different kinds of change.
In the model, the leaf begins with eight water units and receives three more during the interval. The more-open state loses six, leaving five. The more-closed state loses two, leaving nine. Its potential carbon-dioxide admission indices are eight and three respectively. Those gas indices use different units from the water inventory; subtracting gas index from water would produce a meaningless quantity.
Neither state has an assigned amount of realised photosynthesis, growth or offspring. Lower water loss therefore does not by itself prove higher fitness, and higher gas admission does not by itself prove higher carbon gain. The comparison identifies simultaneous consequences to investigate rather than choosing a universally superior surface state.
Environmental change can interrupt many histories
A mass extinction involves unusually extensive loss of lineages across broad regions over a geologically limited interval. Identifying it requires fossil comparisons and attention to dating, preservation and sampling. A local habitat disappearing is not automatically a global extinction, and a lineage's decline in abundance is not the same as its complete loss.
The end-Permian crisis, around 252 Ma in the rounded context used here, has been studied by combining dated geological sections, fossil evidence and environmental indicators. Shen and colleagues provide an example of that combined approach. Burgess and colleagues examine the timing of Siberian Traps sill emplacement as a mechanism linked to environmental disruption. These studies supply specific evidence and hypotheses; the chapter does not assign one simple cause to every extinction.
At the Cretaceous–Paleogene boundary, 66 Ma on the selected chart, Schulte and colleagues synthesised the association of the Chicxulub impact, a geographically widespread boundary record and biological losses. A useful explanation links a disturbance to effects on organisms and food webs. Merely placing an impact and an extinction near each other on a page would not supply those causal links.
A recovering count need not restore the old community
The invented community contains twenty lineage identities. Five survive the loss interval and fifteen do not. Ten new lineages later appear, while all five original survivors persist, so later richness is fifteen. The model assigns the complete inventory; it includes no missing fossils or uncertain detections.
A later total of fifteen is 75% of the initial count, but only five original lineages remain. No extinct A identity returns. New B identities can occupy similar broad roles without becoming the extinct lineages. A recovered number and recovered historical composition therefore answer different questions.
The assigned guilds also change. Initially there are five producer, eight grazer and seven predator lineages. Immediately after loss there are two, two and one. Later there are four, eight and three. The grazer count returns to eight while producer and predator counts do not. Even matching one guild's count does not show restored interactions, abundance or ecosystem function.
Richness and historical composition can recover differently
Read the diagram in words
Initially twenty A identities have guild counts of five producers, eight grazers and seven predators. A01, A02, A06, A07 and A14 survive: two producers, two grazers and one predator. Later ten B identities join those five, giving fifteen lineages with guild counts four, eight and three. Survival connections follow the same five A identities through all stages; B identities are new.
| Lineage identity | Assigned guild | Lineage origin |
|---|---|---|
| A01 | Producer lineages | A identity: original lineage |
| A02 | Producer lineages | A identity: original lineage |
| A03 | Producer lineages | A identity: original lineage |
| A04 | Producer lineages | A identity: original lineage |
| A05 | Producer lineages | A identity: original lineage |
| A06 | Grazer lineages | A identity: original lineage |
| A07 | Grazer lineages | A identity: original lineage |
| A08 | Grazer lineages | A identity: original lineage |
| A09 | Grazer lineages | A identity: original lineage |
| A10 | Grazer lineages | A identity: original lineage |
| A11 | Grazer lineages | A identity: original lineage |
| A12 | Grazer lineages | A identity: original lineage |
| A13 | Grazer lineages | A identity: original lineage |
| A14 | Predator lineages | A identity: original lineage |
| A15 | Predator lineages | A identity: original lineage |
| A16 | Predator lineages | A identity: original lineage |
| A17 | Predator lineages | A identity: original lineage |
| A18 | Predator lineages | A identity: original lineage |
| A19 | Predator lineages | A identity: original lineage |
| A20 | Predator lineages | A identity: original lineage |
| Lineage identity | Assigned guild | Lineage origin |
|---|---|---|
| A01 | Producer lineages | A identity: original lineage |
| A02 | Producer lineages | A identity: original lineage |
| A06 | Grazer lineages | A identity: original lineage |
| A07 | Grazer lineages | A identity: original lineage |
| A14 | Predator lineages | A identity: original lineage |
| Lineage identity | Assigned guild | Lineage origin |
|---|---|---|
| A01 | Producer lineages | A identity: original lineage |
| A02 | Producer lineages | A identity: original lineage |
| A06 | Grazer lineages | A identity: original lineage |
| A07 | Grazer lineages | A identity: original lineage |
| A14 | Predator lineages | A identity: original lineage |
| B01 | Producer lineages | B identity: new lineage |
| B02 | Producer lineages | B identity: new lineage |
| B03 | Grazer lineages | B identity: new lineage |
| B04 | Grazer lineages | B identity: new lineage |
| B05 | Grazer lineages | B identity: new lineage |
| B06 | Grazer lineages | B identity: new lineage |
| B07 | Grazer lineages | B identity: new lineage |
| B08 | Grazer lineages | B identity: new lineage |
| B09 | Predator lineages | B identity: new lineage |
| B10 | Predator lineages | B identity: new lineage |
| Stage | Producer lineages | Grazer lineages | Predator lineages | Total lineage count |
|---|---|---|---|---|
| Before loss | 5 | 8 | 7 | 20 |
| After loss | 2 | 2 | 1 | 5 |
| Later community | 4 | 8 | 3 | 15 |
| From | To | Relationship |
|---|---|---|
| Before loss · A01 | After loss · A01 | Original lineage persists |
| After loss · A01 | Later community · A01 | The same survivor persists |
| Before loss · A02 | After loss · A02 | Original lineage persists |
| After loss · A02 | Later community · A02 | The same survivor persists |
| Before loss · A06 | After loss · A06 | Original lineage persists |
| After loss · A06 | Later community · A06 | The same survivor persists |
| Before loss · A07 | After loss · A07 | Original lineage persists |
| After loss · A07 | Later community · A07 | The same survivor persists |
| Before loss · A14 | After loss · A14 | Original lineage persists |
| After loss · A14 | Later community · A14 | The same survivor persists |
Fifteen original identities absent after loss
Later richness = 15/20 = 75% of initial count
No extinct original identity returns
A completely known invented community, with lineage identities and assigned ecological guilds. Before: 20 lineages; after loss: five original survivors; later: the same five plus ten new lineages. No fossil sampling error, actual extinction event, elapsed geological duration or return of extinct original lineages is assigned.
A changing Earth does not follow a single progress line
Land occupation, organelle integration and multicellular organisation opened possibilities in particular lineages; they did not make every other way of living obsolete. Microbial life persists through these transitions. Extinctions remove histories as well as providing ecological circumstances in which survivors and new lineages may diversify.
The chapter's dates, boundaries and models each answer a limited question. A boundary helps compare ages; a budget exposes simultaneous constraints; a lineage account distinguishes loss from replacement. Keep these tools separate until the evidence justifies their connection.
To read a proposed history, ask what is observed, what is inferred, which scale is being used and which alternatives remain. This habit carries into the next chapters on particular organisms and into later ecology: today's diversity is the surviving result of many interacting histories.
Worked example
Count loss, later richness and identity separately
Begin with twenty A lineages and retain A01, A02, A06, A07 and A14. Five survive, so fifteen are extinct within the fully specified account. The initial loss fraction is 15/20=75%; survival is 5/20=25%. Those percentages concern original identities, not individual organisms or biomass.
Add ten B lineages later. The total is 5+10=15, or 75% of initial richness. That second 75% is a different comparison from the 75% initial loss. Five of the later fifteen identities are original survivors and ten are new.
Two new producers, six new grazers and two new predators produce later guild counts of four, eight and three. The sum is fifteen. Returning grazer richness has not restored the seven original predator identities, nor has the model supplied measurements of feeding relationships or the time required for recovery.
Check your understanding
If water input falls from three units to one, calculate the two leaf inventories. Does this establish which state yields more offspring?
Show reasoning
More-open inventory is 8+1−6=3 units; more-closed inventory is 8+1−2=7 units. The model still gives no realised photosynthesis or offspring data, so these inventories do not determine fitness. It compares water consequences under an assigned input.
A later total of fifteen lineages equals 75% of the initial twenty. How many extinct original lineages have returned?
Show reasoning
None. Five A lineages survive throughout and ten B lineages are new. Fifteen initial A identities are absent afterward. The later richness percentage measures the total count, not restoration of original identities.
Why can neither a boundary date nor a small local fossil collection alone establish the mechanism of a mass extinction?
Show reasoning
A date constrains timing, and a local collection records particular preserved organisms. A global loss and its mechanism require wider comparisons, sampling and preservation checks, and evidence connecting the disturbance with biological effects. Matching times is useful but does not supply every causal link.
What to carry forward
Environmental transitions change constraints and surviving histories. Follow water and gas separately, and follow lineage identity and ecological structure alongside total diversity.
References
Resources supporting this lesson’s explanations and examples.
- Fragments of the earliest land plants (Nature 425, 282–285, 2003)Charles H. Wellman, Peter L. Osterloff and Uzma MohiuddinResearch abstract
- Biology 2e: Early Plant Life (2018; section 25.1)Mary Ann Clark, Matthew Douglas and Jung ChoiOpen university textbook
- Calibrating the end-Permian mass extinction (Science 334, 1367–1372, 2011)Shu-zhong Shen and colleaguesResearch abstract
- Initial pulse of Siberian Traps sills as the trigger of the end-Permian mass extinction (Nature Communications 8, 164, 2017)S. D. Burgess, J. D. Muirhead and S. A. BowringResearch abstract
- The Chicxulub asteroid impact and mass extinction at the Cretaceous-Paleogene boundary (Science 327, 1214–1218, 2010)Peter Schulte and colleaguesResearch abstract
- International Chronostratigraphic Chart (June 2026)International Commission on StratigraphyInternational standard chart · PDF