Thursday, September 3, 2026

THE TELEMETRY OF LIFE:Multistream Environmental Sensing, Biological Equilibrium, and Closed-Loop Control in Organismal Behavior

THE TELEMETRY OF LIFE:

Multistream Environmental Sensing, Biological Equilibrium, and Closed-Loop Control in Organismal Behavior

DOI: [to be assigned]

John Swygert

September 3, 2026


Abstract

Organisms do not merely receive information about their environments. They continuously use external and internal information to regulate physiological state, select behavior, orient movement, exploit environmental energy, avoid danger, acquire resources, reproduce, and maintain conditions compatible with life. Yet biological behavior is often described in terms of individual senses or final outcomes—migration, navigation, thermoregulation, foraging, dispersal—rather than as the product of multiple simultaneous information streams participating in closed biological control loops.

This paper proposes a framework termed the telemetry of life: the continuous acquisition, integration, and biological use of external and internal state information by organisms. The term telemetry is used here as a systems analogy and should not be confused with conventional wildlife telemetry, in which instruments remotely transmit measurements. Biological organisms do not literally transmit all sensory information to an external receiver. Rather, they possess distributed streams of environmental and physiological information that can function analogously to telemetry within a control architecture.

The framework begins with a visually striking comparison between ballooning spiders and the deep-sea bigfin squid, Magnapinna spp. Ballooning spiders use silk to couple themselves to atmospheric forces and can behaviorally evaluate environmental conditions before takeoff. Magnapinna possesses an unusual morphology characterized by large fins, extended proximal appendages, and extraordinarily long distal filaments. The functional significance of its characteristic posture remains incompletely understood. The superficial resemblance between these organisms does not establish convergent evolution or a shared locomotor mechanism. It does, however, motivate a testable biomechanical question: can extended and filamentous morphologies provide useful ways of coupling organisms to moving fluids, while biological information determines when and how that coupling is exploited?

From this comparison, a broader model is developed in which behavior arises through repeated cycles:

[ \text{environmental state} \rightarrow \text{biological detection} \rightarrow \text{state integration} \rightarrow \text{action} \rightarrow \text{new environmental relationship} \rightarrow \text{new detection}. ]

Within fluid environments, this framework produces a specific hypothesis. Atmospheres and oceans contain vertically and horizontally structured velocity fields rather than uniform currents. An organism may therefore reduce the energetic cost of horizontal travel by maneuvering between moving fluid layers. Temperature, pressure, oxygen, salinity, chemistry, flow, light, magnetic information, internal energy state, and other variables could provide simultaneous control inputs. Repeated local responses intended to maintain or restore biological equilibrium could consequently generate large-scale trajectories without requiring a human-like representation of the complete route.

The framework is extended beyond locomotion to homeostasis, habitat selection, foraging, predator avoidance, reproduction, microbial behavior, plant responses, and ecological interaction. It generates an empirical program in which real organismal telemetry and environmental measurements are used to construct artificial agents possessing only biologically plausible information streams. Sensory channels can then be removed, combined, altered, or placed in conflict to determine which information is sufficient to reproduce observed behavior.

The central proposition is:

Morphology determines how an organism can interact with physical forces; biological telemetry provides information about its relationship to those forces and to its internal state; closed-loop control transforms that information into actions that can maintain life and generate complex behavior.


1. Introduction

Every living organism exists inside changing physical conditions.

Temperature changes.

Light changes.

Chemical concentrations change.

Water availability changes.

Air and water move.

Resources appear and disappear.

Predators approach.

Prey move.

Internal energy stores decline.

Cells experience changing molecular conditions.

The organism itself also changes continuously.

Life therefore presents a fundamental control problem:

[ \text{How can a biological system remain viable while both itself and its environment are changing?} ]

The answer necessarily involves information.

An organism must detect at least some biologically relevant differences, directly or indirectly, and respond to them.

This does not require consciousness.

It does not require a nervous system.

It does not require symbolic reasoning.

It requires biological mechanisms capable of coupling detectable differences to consequential responses.

The framework developed here treats those simultaneously changing information streams as the telemetry of life.


2. What Is Meant by Biological Telemetry?

In engineering and field biology, telemetry conventionally refers to measurements collected at one location and transmitted elsewhere for observation.

That is not the literal meaning proposed here.

The term biological telemetry is used as a systems-level analogy for the streams of information available within an organism concerning:

  1. the external environment,
  2. the organism's own internal condition,
  3. other organisms,
  4. its movement relative to the environment,
  5. and changes occurring through time.

A useful distinction is therefore:

[ \text{instrumental telemetry} \neq \text{biological telemetry as defined here}. ]

The latter describes information entering and circulating through biological control architectures.

Examples include information associated with:

[ T=\text{temperature} ]

[ P=\text{pressure} ]

[ C=\text{chemical conditions} ]

[ L=\text{light} ]

[ F=\text{fluid movement} ]

[ M=\text{magnetic-field properties} ]

[ Q=\text{electrical conditions} ]

[ V=\text{mechanical vibration} ]

[ O=\text{oxygen availability} ]

[ S=\text{salinity} ]

together with internal variables such as energy state, hydration, nutrient status, metabolic state, damage, reproductive condition, and other physiological variables.

No claim is made that every organism measures all of these.

The available streams are organism-specific.


3. From Sensory Reality to Biological Control

Previous formulations of organismal informational reality can be represented as:

[ R_i=\Phi_i(E), ]

where:

  • E is the physical environment,
  • \Phi_i is the detection architecture of organism i,
  • R_i is the portion of environmental information biologically available to that organism.

But detection alone is insufficient to explain behavior.

An organism must somehow transform available information into biological response.

Let:

[ D_i(t)=\Phi_i[E(t)] ]

represent external information detected at time t.

Let:

[ I_i(t) ]

represent internal-state information.

Let:

[ H_i(t) ]

represent biologically relevant recent history, memory, adaptation, or prior state where applicable.

The organism's operational state can then be represented:

[ X_i(t)=\Psi_i[D_i(t),I_i(t),H_i(t)]. ]

Action becomes:

[ A_i(t)=\pi_i[X_i(t)]. ]

That action changes the organism's relationship with the environment:

[ A_i(t)\rightarrow E_i(t+1). ]

The organism consequently receives new information:

[ E_i(t+1)\rightarrow D_i(t+1). ]

The complete architecture is therefore recursive:

[ E_t \rightarrow D_t \rightarrow X_t \rightarrow A_t \rightarrow E_{t+1} \rightarrow D_{t+1}. ]

Life operates within loops.


4. A Visual Observation: Spider and Bigfin Squid

A useful starting point comes from two organisms inhabiting dramatically different environments.

The first is a ballooning spider.

The second is the deep-sea bigfin squid:

[ \textit{Magnapinna}\ \text{spp.} ]

They are phylogenetically distant and occupy entirely different ecological settings.

Yet certain images of Magnapinna produce a striking superficial resemblance to a spider: a relatively centralized body architecture surrounded by long, thin, extended structures.

The resemblance itself proves nothing.

It does not demonstrate common ancestry for the morphology.

It does not establish convergent evolution.

It does not demonstrate that the squid's appendages function like ballooning silk.

But scientific hypotheses often begin with noticing a pattern and asking whether it contains useful information.

The appropriate question is therefore not:

Do these organisms look similar because they use the same locomotor mechanism?

The appropriate question is:

Could some aspects of superficially similar extended geometries provide analogous fluid-dynamic advantages in different fluid environments?

That question can be tested.


5. The Atmospheric Example: Ballooning Spiders

Spider ballooning provides a demonstrated example of an organism exploiting environmental physical forces for transportation.

Ballooning spiders climb to an exposed location, release silk, and can become airborne through interaction between the silk and atmospheric forces.

Experiments and observations show that the phenomenon is more sophisticated than simply describing the spider as an inert particle carried randomly by wind.

Studies of ballooning spiders have documented behavioral evaluation of wind conditions before launch. Experiments with Erigone spp. have additionally shown that atmospheric-strength electric fields can elicit pre-ballooning behavior and takeoff, and mechanosensory hairs respond to weak electric fields.

Ballooning therefore involves at least two scientifically important concepts:

[ \text{environmental force} ]

and

[ \text{biological detection of environmental conditions}. ]

The spider does not generate the atmospheric transportation field.

It exploits it.

Its silk provides physical coupling.

Its behavior affects when that coupling begins.

Thus:

[ \text{environmental information} \rightarrow \text{launch decision} \rightarrow \text{fluid/electrostatic coupling} \rightarrow \text{transport}. ]

This immediately distinguishes passive propulsion from passive behavior.

An organism can receive most of its transportation energy from the environment while actively controlling its entry into that transportation system.


6. The Marine Example: Bigfin Squid

Bigfin squid of the genus Magnapinna are rarely observed deep-sea cephalopods distinguished by large fins and extraordinarily elongated arm and tentacle filaments.

A characteristic configuration involves proximal appendages extending outward before extremely long distal filaments descend through the surrounding water.

The function of this distinctive configuration remains incompletely resolved. Feeding has been proposed as one possible function because of the adhesive characteristics of the filaments and comparisons with other deep-sea squid.

Consequently, this paper does not propose that the long filaments evolved primarily for transport.

Instead, it proposes a question:

Do the extended appendages and filaments have measurable consequences for drag, stability, orientation, current coupling, flow sensing, vertical positioning, or energetic expenditure in moving water?

The answer could be yes, no, or functionally insignificant.

Each outcome would be scientifically informative.


7. Morphology as an Interface with Environmental Energy

An organism's morphology determines how physical forces act upon it.

For an organism in a fluid, relevant properties include:

  • projected area,
  • drag coefficient,
  • buoyancy,
  • density,
  • appendage geometry,
  • flexibility,
  • orientation,
  • surface properties,
  • center of mass,
  • center of buoyancy,
  • and the surrounding flow regime.

Thus morphology can be represented as part of a physical coupling function:

[ K_i=K(M_i,F), ]

where:

  • M_i represents organismal morphology,
  • F represents the surrounding fluid field,
  • K_i represents the resulting physical coupling.

The important hypothesis is therefore broader than either spiders or squid:

Extended or filamentous biological structures may sometimes increase, regulate, or otherwise alter coupling between an organism and moving fluid, although their primary evolutionary functions may be entirely different or multifunctional.

The spider and Magnapinna serve as visually intuitive endpoints of this larger question.


8. Air and Water Are Both Fluids—but They Are Not Equivalent

The comparison must not obscure major physical differences.

Air and seawater differ substantially in:

  • density,
  • viscosity,
  • buoyancy,
  • pressure structure,
  • compressibility,
  • turbulence,
  • conductivity,
  • and the forces acting on organisms and filaments.

The relevant Reynolds-number regimes may also differ dramatically between structures and organisms.

Therefore:

[ \text{atmospheric ballooning} \neq \text{underwater ballooning}. ]

The proposed analogy is structural:

[ \text{organism} + \text{extended geometry} + \text{moving fluid} + \text{environmental information} ]

rather than a claim of identical mechanics.

The comparison asks whether evolution can exploit environmental movement through different biological solutions operating under different physical regimes.


9. The Transportation-Network Hypothesis

Atmospheres and oceans do not move uniformly.

They contain structured velocity fields:

[ \mathbf{v}(x,y,z,t). ]

Flow direction and velocity can vary with:

  • horizontal location,
  • altitude or depth,
  • time,
  • temperature,
  • density,
  • pressure,
  • topography,
  • tides,
  • atmospheric structure,
  • ocean stratification,
  • and turbulence.

An organism embedded in such a system therefore exists within a moving transportation network.

At one vertical position:

[ z_1:\mathbf{v}_1. ]

At another:

[ z_2:\mathbf{v}_2. ]

And:

[ \mathbf{v}_1\neq\mathbf{v}_2. ]

The flows may differ in speed and direction.

This produces the moving-highway hypothesis:

For some organisms, energetically efficient horizontal displacement may be achieved partly by controlling vertical or local position so that environmental fluid motion supplies a substantial portion of horizontal transportation.

The organism need not propel itself across the entire journey.

It may need to maneuver between environmental transportation layers.


10. Passive Transport Does Not Mean Passive Navigation

Consider a human transportation analogy.

A passenger traveling by train does not generate the locomotive force.

The important actions are:

  1. choosing a route,
  2. reaching the appropriate station,
  3. boarding,
  4. transferring when necessary,
  5. and leaving the system at the appropriate point.

Environmental transport can operate similarly in principle.

The organism supplies:

[ E_{\text{control}} ]

while the environment supplies:

[ E_{\text{transport}}. ]

When:

[ E_{\text{transport}}\gg E_{\text{control}}, ]

large displacement can occur for comparatively little organism-generated locomotor energy.

This suggests an important distinction:

[ \boxed{\text{passive propulsion}\neq\text{passive navigation}}. ]

An organism can exploit passive transport through active decisions.


11. The Multistream Problem

How might an organism determine when to change position?

A marine organism could potentially possess biologically accessible information related to:

[ T=\text{temperature}, ]

[ P=\text{pressure/depth}, ]

[ O=\text{oxygen}, ]

[ S=\text{salinity}, ]

[ F=\text{fluid velocity}, ]

[ C=\text{chemical conditions}, ]

[ L=\text{light}, ]

[ M=\text{geomagnetic information}, ]

plus organism-specific biological signals.

Its internal state may simultaneously provide:

[ I={\text{energy, hydration, metabolic demand, reproductive state, stress, damage,\ldots}}. ]

Behavior can therefore depend upon a multivariable state:

[ A_t=f(T,P,O,S,F,C,L,M,I,H). ]

The organism need not consciously calculate this function.

Evolution, physiology, neural processing where present, and other biological regulatory systems can embody it.


12. Equilibrium as a Control Objective

Many biological systems regulate variables around viable ranges.

Let a biologically preferred or viable state be represented:

[ X^*. ]

Current state is:

[ X_t. ]

Deviation is:

[ \epsilon_t=X_t-X^*. ]

A regulatory response can act to reduce:

[ |\epsilon_t|. ]

In reality, biological regulation usually involves ranges, tradeoffs, nonlinearities, multiple competing variables, and changing set points rather than a single perfect equilibrium.

Nevertheless, the control formulation captures a central principle:

[ \text{detect deviation} \rightarrow \text{respond} \rightarrow \text{measure new state}. ]

This is the architecture of feedback.


13. Temperature as a Hypothetical Driver

Consider a simplified marine example.

An organism occupies water at temperature:

[ T_t. ]

Its viable or preferred temperature range is:

[ [T_{\min},T_{\max}]. ]

Suppose:

[ T_t<T_{\min}. ]

A biological response produces vertical movement:

[ A_t=\text{ascend} ]

or:

[ A_t=\text{descend}, ]

depending upon local ocean structure.

The organism enters another water mass.

Temperature changes:

[ T_{t+1}. ]

But something else changes simultaneously:

[ F_t\rightarrow F_{t+1}. ]

The new depth contains a different current.

Thus a maneuver initiated in response to temperature can produce horizontal displacement.

The causal chain becomes:

[ \text{temperature deviation} \rightarrow \text{vertical movement} \rightarrow \text{current change} \rightarrow \text{horizontal transport}. ]

Repeated over time, this could generate a large-scale trajectory.

This is a hypothesis, not a claim that Magnapinna or any particular organism uses this mechanism.


14. Equilibrium-Seeking Migration

The preceding example suggests a broader possibility.

Some large-scale movement could emerge from repeated local regulation:

[ \text{local state correction} + \text{environmental structure} \rightarrow \text{large-scale trajectory}. ]

An outside observer sees:

[ \text{migration}. ]

The organism's control architecture may instead be repeatedly solving local problems:

[ \text{too cold} ]

[ \text{oxygen declining} ]

[ \text{chemical cue strengthening} ]

[ \text{current unfavorable} ]

[ \text{light inappropriate} ]

[ \text{pressure changing} ]

[ \text{magnetic condition inconsistent} ]

[ \text{internal energy declining}. ]

No single variable need control the journey.

The trajectory could emerge from multistream control.


15. Geography and Equilibrium Need Not Be Alternatives

A crucial point follows.

Navigation based upon geographical information and movement based upon physiological regulation are not mutually exclusive.

An organism could possess information related to location or direction while simultaneously regulating physiological state.

Thus:

[ A_t= f( \text{geographic information}, \text{environmental state}, \text{internal state} ). ]

For example, a migrating organism could maintain a general directional tendency while selecting depths or altitudes according to temperature, oxygen, currents, winds, or resource conditions.

This is more realistic than requiring a single sensory mechanism to explain an entire migration.


16. Salmon as a Multistream Example

Salmon provide a useful established example of multimodal navigation.

Evidence supports the use of olfactory information in natal-stream recognition and geomagnetic information in large-scale navigation, while environmental variables such as temperature, flow, salinity, and other conditions also affect salmon biology and movement.

The important conceptual lesson is not that one channel has been identified as the navigation system.

It is that biological navigation can be sequential and multimodal.

A salmon can therefore be modeled not as:

[ \text{destination}\rightarrow\text{movement} ]

but as:

[ A_t=f(M,C,F,T,S,I,H,\ldots). ]

The scientific challenge becomes determining the relative contribution and interaction of those channels.


17. From Destination Thinking to Control Thinking

Human observers naturally describe animal movement according to destinations.

“The salmon is returning home.”

“The bird is migrating south.”

“The spider is dispersing.”

“The marine animal is moving toward warmer water.”

Those descriptions may be accurate at the ecological level while obscuring the control mechanism.

A more mechanistic question is:

What information is available to the organism at this moment, what internal variables are changing, and what action follows?

Then ask the same question at:

[ t+1, ]

and:

[ t+2. ]

A complete migration may emerge from thousands or millions of local control events.


18. The Organism Does Not Need the Human Map

Suppose a simulated organism is told:

[ \text{Travel to coordinate }(x_d,y_d). ]

Success reveals little about biological navigation because the destination has been supplied explicitly.

Instead, remove the coordinate.

Give the agent only biologically plausible inputs:

[ D_t. ]

Allow it to respond through:

[ A_t=\pi(D_t,I_t,H_t). ]

Then determine whether:

[ (x_t,y_t,z_t)\rightarrow(x_d,y_d,z_d) ]

emerges.

If it does, the modeled information may be sufficient.

If it does not, the model may lack:

  • a sensory channel,
  • an internal variable,
  • memory,
  • an appropriate control rule,
  • environmental resolution,
  • developmental information,
  • social information,
  • or some other relevant factor.

Failure becomes informative.


19. Maneuvering Versus Propulsion

The framework suggests separating two concepts often merged under locomotion.

Propulsion

Energy that produces displacement.

Maneuvering

Control that changes how displacement occurs.

For an organism exploiting environmental flow:

[ \text{net displacement}

\text{self-propulsion} + \text{environmental transport}. ]

But biological control can determine the weighting of these terms.

A small vertical maneuver may yield enormous horizontal displacement if it places the organism inside a strong current.

Therefore the energetic cost of navigation cannot always be inferred from travel distance alone.


20. Morphology + Telemetry + Environmental Energy

The full framework can now be stated:

[ \boxed{ \text{Behavioral outcome}

f( \text{morphology}, \text{telemetry}, \text{control}, \text{environmental energy} ) } ]

Morphology determines possible physical interactions.

Telemetry supplies information.

Control transforms information into response.

Environmental energy can amplify the consequences of that response.

The spider provides a demonstrated atmospheric example of this general architecture.

The Magnapinna comparison raises the question of how far analogous principles may extend into marine systems.

Many other organisms provide additional cases.


21. Beyond Spiders and Squid

The spider–bigfin-squid comparison is illustrative rather than unique.

Environmental transport is relevant to:

  • aerial arthropods,
  • plankton,
  • jellyfish,
  • larvae,
  • spores,
  • seeds,
  • microorganisms,
  • fishes,
  • marine invertebrates,
  • birds using thermals and wind,
  • and numerous other organisms.

The balance between active propulsion and environmental transport varies enormously.

The general question remains:

How much biological control can be achieved by sensing and exploiting energy already present in the environment?


22. Telemetry for Supporting Life

Movement is only one application.

The same architecture supports basic biological viability.

Consider:

[ \text{temperature telemetry} \rightarrow \text{thermoregulatory response}, ]

[ \text{water-status telemetry} \rightarrow \text{water conservation/acquisition}, ]

[ \text{energy telemetry} \rightarrow \text{foraging}, ]

[ \text{oxygen telemetry} \rightarrow \text{respiratory or positional response}, ]

[ \text{damage telemetry} \rightarrow \text{repair/avoidance response}. ]

The organism continually adjusts itself relative to changing conditions.

Life is therefore not merely structure.

It is regulated structure.


23. Plants and Distributed Biological Control

The framework is not limited to animals.

Plants continuously respond to environmental information involving:

  • light,
  • gravity,
  • moisture,
  • temperature,
  • mechanical stimulation,
  • chemical conditions,
  • nutrient availability,
  • pathogens,
  • herbivory,
  • and neighboring organisms.

Growth itself can function as a long-timescale control response.

Roots change direction.

Shoots change orientation.

Stomata regulate gas exchange.

Development changes with environmental conditions.

The relevant timescale differs from rapid animal maneuvering, but the architecture remains:

[ \text{detect} \rightarrow \text{integrate} \rightarrow \text{respond} \rightarrow \text{detect again}. ]


24. Microorganisms and Gradient Navigation

Microbial chemotaxis provides an especially clear demonstration that complex-looking navigation need not require a cognitive map.

A microorganism can alter movement according to changes in chemical conditions.

Local sampling produces directional bias.

Repeated local responses generate movement through a chemical landscape.

This offers an important analogy for the larger hypothesis:

[ \text{simple local rule} + \text{structured environment} + \text{feedback} \rightarrow \text{complex trajectory}. ]

Large-scale animal navigation may involve vastly more sophisticated systems, but the underlying control principle is general.


25. Internal Telemetry

External sensing alone cannot explain biological behavior.

The organism also has information concerning itself.

Let:

[ I_t= {i_1,i_2,\ldots,i_m}. ]

These variables can include physiological conditions relevant to:

  • energy,
  • hydration,
  • oxygenation,
  • temperature,
  • nutrient status,
  • reproductive condition,
  • injury,
  • immune activity,
  • metabolic state,
  • and other internal processes.

Behavior therefore depends upon the relationship:

[ A_t=f(D_t,I_t). ]

The same external environment can generate different behavior because:

[ I_t\neq I_{t+1}. ]

A hungry organism and a satiated organism can inhabit the same physical environment while making different decisions.


26. Equilibrium Is Dynamic

The word equilibrium must be used carefully.

Living systems are not generally static equilibrium systems.

They are dynamic, energy-consuming systems maintaining viable states far from thermodynamic equilibrium.

The relevant biological concept is therefore closer to:

  • homeostasis,
  • allostasis,
  • regulation,
  • dynamic stability,
  • viable operating range,
  • and state-dependent control.

Thus the proposed equilibrium model should be understood as shorthand for:

[ X_t\in\mathcal{V}, ]

where:

[ \mathcal{V} ]

is a viable region of biological state space.

Behavior acts partly to keep the organism within, or return it toward, that region.


27. Competing Equilibria and Tradeoffs

Organisms frequently cannot optimize every variable simultaneously.

Warmer water may contain less oxygen.

A favorable current may move away from food.

A resource-rich habitat may contain predators.

A thermally favorable altitude may have unfavorable wind.

An organism therefore faces a multi-objective control problem:

[ J= w_1J_T+ w_2J_O+ w_3J_E+ w_4J_P+ w_5J_R+\cdots ]

where the weights:

[ w_i ]

may themselves change with internal state.

Behavior can therefore appear inconsistent when viewed through only one variable while being rational within a multivariable biological control architecture.


28. Cue Conflict

This creates a powerful experimental method.

Present conflicting information.

For example:

[ T\rightarrow A ]

while:

[ M\rightarrow B. ]

Which input dominates?

Then vary internal state.

Does hunger change the weighting?

Does reproductive state?

Does developmental stage?

Does prior experience?

Cue-conflict experiments can reveal the hidden weighting structure of biological telemetry.


29. Sensory Ablation

Another method is informational removal.

Let the full detected state be:

[ D={T,P,O,S,F,C,M,L}. ]

Remove magnetic information:

[ D^{(-M)}. ]

Remove temperature:

[ D^{(-T)}. ]

Remove flow:

[ D^{(-F)}. ]

Compare resulting behavior.

If removal of one channel causes predictable degradation, that channel likely contributes to the control architecture.

If behavior remains unchanged, redundancy may exist.

Biological control may therefore be robust because several telemetry streams partially overlap.


30. Redundant Telemetry

Redundancy is potentially critical.

Suppose:

[ M ]

and:

[ C ]

both provide information correlated with location.

If one becomes unreliable, the other may still support navigation.

Similarly:

[ T, S, F, P ]

may jointly identify particular water masses better than any variable alone.

The organism may therefore exploit environmental signatures rather than isolated measurements.

Define:

[ \Sigma_t=(T,S,P,O,C,F,\ldots). ]

A location or habitat may possess a characteristic multidimensional signature.

Navigation could then depend partly upon recognizing trajectories through signature space rather than explicit geographic coordinates.


31. Environmental Signatures as Biological Coordinates

This possibility deserves special attention.

Humans represent geography primarily using:

[ \text{latitude}, \text{longitude}, \text{altitude/depth}. ]

Another organism need not.

Its effective coordinates could be combinations of:

[ T, S, M, C, F, L, P. ]

Thus biological geography may sometimes be represented as:

[ G_i=\Gamma_i(E), ]

where:

[ G_i ]

is an organism-specific navigational coordinate system.

A salmon's informational ocean may therefore contain landmarks that are invisible to humans without instruments.

A spider's atmosphere may contain usable structures that a human standing nearby does not consciously perceive.

The physical world is shared.

The navigational coordinate systems need not be.


32. Testing the Moving-Highway Hypothesis

The moving-highway hypothesis can be tested directly.

For a marine organism, measure:

[ (x,y,z,t) ]

together with:

[ \mathbf{v}(x,y,z,t), ]

temperature, pressure, salinity, oxygen, chemistry, light, magnetic information, and relevant internal variables where possible.

Then determine whether vertical movements precede predictable changes in horizontal displacement.

Compare:

[ \Delta z_t ]

with:

[ \Delta \mathbf{v}_{t+1}. ]

If organisms repeatedly enter flow layers that improve displacement relative to a biologically relevant direction or state, the pattern would support active flow selection.

Randomized or null models could determine whether the observed association exceeds chance expectation.


33. Testing the Morphological Hypothesis

The spider–Magnapinna comparison can likewise be made experimentally rigorous.

Construct physical or computational models representing:

  1. compact morphology,
  2. extended appendage morphology,
  3. filamentous morphology,
  4. alternative orientations,
  5. altered appendage lengths,
  6. altered flexibility.

Expose these models to measured or simulated fluid fields.

Measure:

  • drag,
  • stability,
  • rotation,
  • orientation,
  • vertical displacement,
  • lateral displacement,
  • energy required for station keeping,
  • response to shear,
  • and flow-induced deformation.

For Magnapinna, such modeling could determine whether the characteristic geometry produces meaningful hydrodynamic consequences even if feeding remains its primary function.

A negative result would be equally important.


34. Predictions

The framework produces several testable predictions.

Prediction 1

Some organisms exploiting environmental flows should exhibit behavioral transitions correlated with measurable changes in environmental information before entering or leaving particular flow regimes.

Prediction 2

Vertical movement should sometimes produce disproportionately large horizontal displacement because of stratified current or wind fields.

Prediction 3

Models containing multiple biologically realistic telemetry streams should reproduce observed trajectories better than equivalent single-cue models where behavior is genuinely multimodal.

Prediction 4

Cue-conflict experiments should reveal state-dependent weighting among information channels.

Prediction 5

Removing biologically important telemetry streams from simulations should degrade behavioral performance in characteristic ways.

Prediction 6

Morphologies containing extended or filamentous structures should produce measurable changes in fluid coupling relative to geometrically simplified controls, although the sign and biological importance of those effects must be determined experimentally.

Prediction 7

Some apparently destination-directed movement should be reproducible without supplying agents with explicit destination coordinates if environmental information and control rules are sufficient.


35. Artificial Organisms as Experimental Models

Artificial agents provide an unusually powerful way to test these propositions.

Construct a physical simulation:

[ E(x,y,z,t). ]

Create an artificial organism with morphology:

[ M_i. ]

Give it only biologically plausible inputs:

[ D_i=\Phi_i(E). ]

Give it internal state:

[ I_i. ]

Allow behavior:

[ A_i=\pi_i(D_i,I_i,H_i). ]

Then ask whether observed biological behavior emerges.

The artificial organism must not receive privileged access to:

  • true global coordinates,
  • complete flow fields,
  • hidden prey locations,
  • destination coordinates,
  • or other information unavailable to the biological organism.

This constraint is essential.

Otherwise the simulation tests the programmer's knowledge rather than the organism's informational architecture.


36. The Fundamental Experiment

A particularly powerful experiment would involve migration.

Select a species with sufficiently rich tracking and environmental data.

Construct a high-resolution environmental reconstruction.

Create an artificial organism possessing only demonstrated or strongly supported sensory channels.

Do not tell it where the destination is.

Initialize it at the observed starting region.

Then allow:

[ E_t \rightarrow D_t \rightarrow X_t \rightarrow A_t \rightarrow E_{t+1}. ]

Ask:

Does the trajectory emerge?

If yes, progressively remove channels.

If no, progressively add biologically plausible information.

The result becomes a search for the minimum sufficient telemetry architecture capable of reproducing the behavior.


37. Minimum Sufficient Telemetry

Define:

[ D^* ]

as the smallest information set capable of reproducing a target behavior within specified accuracy.

Then:

[ D^*= \arg\min_D |D| ]

subject to:

[ \mathcal{B}(D)\geq\theta, ]

where:

  • \mathcal{B}(D) measures behavioral agreement,
  • \theta is a predefined validation threshold.

This transforms questions such as:

How does this animal navigate?

into:

What is the minimum set of information required to reproduce its navigation?

That is experimentally tractable.


38. From Organisms to Ecosystems

No organism operates alone.

Its telemetry includes information generated by other organisms.

Predator signals affect prey.

Prey movement affects predators.

Flowers affect pollinators.

Hosts affect parasites.

Microbes alter chemical landscapes.

Plants modify temperature, humidity, light, chemistry, and structure.

Thus:

[ E_{t+1}

f(E_t,A_1,A_2,\ldots,A_n). ]

Every organism can alter the telemetry available to others.

Closed-loop biological control therefore scales upward into the informational ecosystem.


39. Relationship to the Informational Ecosystem

The informational ecosystem describes overlapping organismal access:

[ \mathcal{R}(E)={R_1,R_2,\ldots,R_n}. ]

The telemetry-of-life framework adds dynamics.

It asks:

What happens next?

For each organism:

[ R_i \rightarrow X_i \rightarrow A_i. ]

Those actions alter:

[ E. ]

The altered environment changes:

[ R_1,R_2,\ldots,R_n. ]

Therefore:

[ \mathcal{R}(E_t) \rightarrow {A_i} \rightarrow E_{t+1} \rightarrow \mathcal{R}(E_{t+1}). ]

The informational ecosystem is not a static map.

It is a continuously updating network of biological control loops.


40. Relationship to Organismal Reality

The simulation of organismal reality asks:

What portion of the physical environment is available to this organism?

The telemetry framework asks:

How is that available information used?

The distinction is:

[ \text{access} \rightarrow \text{control}. ]

An organismal reality becomes biologically consequential when detectable differences influence biological state or action.

Thus the present framework provides a bridge from sensory ecology to behavior, physiology, navigation, and ecological dynamics.


41. Relationship to Human Perspectival Reality

Humans also operate through telemetry.

Vision, audition, vestibular information, proprioception, interoception, touch, temperature, chemical senses, and numerous internal regulatory systems continuously constrain behavior.

Humans supplement these biological streams with technological telemetry:

  • GPS,
  • thermometers,
  • radar,
  • sonar,
  • weather instruments,
  • magnetometers,
  • medical monitors,
  • satellites,
  • environmental sensors.

Technology therefore makes explicit what biology has always required:

[ \text{measure state} \rightarrow \text{compare} \rightarrow \text{decide} \rightarrow \text{act} \rightarrow \text{measure again}. ]

The difference is not the existence of feedback.

It is the architecture through which feedback occurs.


42. Consciousness Is Not Required

Nothing in this framework requires an organism to consciously experience the information it uses.

Therefore:

[ \text{telemetry} \neq \text{conscious perception}. ]

Likewise:

[ \text{decision} ]

is used functionally here and need not imply deliberative cognition.

A regulatory molecular pathway can implement state-dependent selection.

A bacterium can alter movement.

A plant can alter growth.

An animal can execute reflexive behavior.

A human can consciously deliberate.

These processes differ enormously, but all can participate in closed biological feedback.


43. Levels of Biological Control

The telemetry framework can therefore be organized hierarchically:

Molecular

Chemical detection and regulation.

Cellular

Membrane potentials, signaling, metabolic regulation.

Physiological

Homeostatic and allostatic regulation.

Organismal

Movement, feeding, avoidance, reproduction, navigation.

Ecological

Predator-prey, symbiosis, competition, communication.

Population

Dispersal, migration, aggregation.

Evolutionary

Selection acting upon detection and control architectures.

The telemetry of life exists across scales.


44. The Larger Principle

The spider and the bigfin squid return us to the original observation.

Their superficial resemblance may prove biologically irrelevant.

Or particular aspects of their extended geometries may reveal something general about organisms interacting with moving fluids.

Either result is valuable.

What matters is the larger principle exposed by the comparison:

An organism does not need to generate every force responsible for its movement or survival. It can evolve morphology that couples it to environmental forces and biological control systems that exploit information about those forces.

Thus:

[ \text{environment} ]

is not merely something an organism moves through.

It can become part of the organism's effective transportation and control architecture.


45. Conclusion

Life exists inside streams of information.

Some originate outside the organism.

Some originate within it.

Some describe physical conditions.

Some describe other organisms.

Some indicate deviation from viable biological states.

Some reveal opportunities.

Some reveal danger.

The organism continuously changes its relationship with these streams through action.

The fundamental cycle is:

[ \boxed{ E_t \rightarrow D_t \rightarrow X_t \rightarrow A_t \rightarrow E_{t+1} } ]

and then it begins again.

The spider releasing silk into the atmosphere provides a striking example. It can sense environmental conditions, initiate ballooning behavior, physically couple itself to atmospheric forces, and obtain transportation from energy it did not generate.

The bigfin squid provides a provocative comparative question. Its extraordinarily extended appendages and filaments operate in another fluid environment under radically different physical conditions. Their known or proposed functions must not be displaced by unsupported claims. Yet their geometry invites quantitative investigation into drag, stability, orientation, sensing, and interaction with deep-ocean flow.

The comparison therefore produces a broader hypothesis:

[ \boxed{ \text{Morphology} + \text{Telemetry} + \text{Control} + \text{Environmental Energy} \rightarrow \text{Behavior} } ]

The same principle can be examined in migration.

An organism need not necessarily generate all of the energy required to traverse enormous distances.

It may exploit moving atmospheric or oceanic structures.

Its principal energetic contribution may sometimes involve maneuvering between those structures rather than overcoming them.

Temperature may influence one maneuver.

Oxygen another.

Chemistry another.

Current velocity another.

Magnetic information another.

Internal physiological state another.

A large-scale trajectory can therefore potentially emerge from thousands of local decisions made within a changing multivariable environment.

This produces a different way to investigate navigation.

Instead of asking only:

Where does the organism know it is going?

we can ask:

What information is available to the organism now?

What biological state is it regulating?

What action follows from those conditions?

How does that action change the information available next?

Repeated through time, those questions may reconstruct the trajectory.

This approach also avoids assuming that an organism represents geography as humans do.

The human map uses latitude, longitude, and altitude.

Another organism may navigate through combinations of temperature, pressure, chemistry, salinity, light, flow, magnetic information, odor, vibration, or other variables.

Its biological coordinate system may therefore be:

[ G_i=\Gamma_i(E), ]

rather than a human cartographic representation.

The empirical challenge is to discover those coordinates.

This can be approached through measurement, tracking, sensory experiments, cue conflicts, channel ablation, fluid-dynamic modeling, and artificial organisms constrained to biologically plausible information.

Ultimately, the strongest test is simple to state:

Give the simulated organism only what the real organism could plausibly know and determine whether the real behavior still emerges.

If it does, the model has discovered something important.

If it does not, something is missing.

Either result advances the investigation.

Life can therefore be approached not merely as matter organized into organisms, nor merely as organisms sensing environments, but as a hierarchy of continuously operating control systems.

They detect.

They compare.

They regulate.

They maneuver.

They exploit physical forces.

They alter their surroundings.

Then they detect again.

Life does not merely exist within the physical environment. Life continuously measures its relationship to that environment and acts upon the difference.


References

Bradbury, J. W., & Vehrencamp, S. L. (2011). Principles of Animal Communication. Sinauer Associates.

Cho, M., Neubauer, P., Fahrenson, C., & Rechenberg, I. (2018). An observational study of ballooning in large spiders: Nanoscale multifibers enable large spiders' soaring flight. PLOS Biology, 16(6), e2004405. DOI: 10.1371/journal.pbio.2004405.

Dusenbery, D. B. (1992). Sensory Ecology: How Organisms Acquire and Respond to Information. W. H. Freeman.

Jamieson, A. J., et al. (2026). Global distribution and depth of the bigfin squid Magnapinna spp. Marine Biology, 173, Article 172.

Lohmann, K. J., Goforth, K. M., Mackiewicz, A. G., Lim, D. S., & Lohmann, C. M. F. (2022). Magnetic maps in animal navigation. Journal of Comparative Physiology A, 208, 41–67. DOI: 10.1007/s00359-021-01529-8.

Lohmann, K. J., Lohmann, C. M. F., & Endres, C. S. (2008). The sensory ecology of ocean navigation. Journal of Experimental Biology, 211, 1719–1728. DOI: 10.1242/jeb.015792.

Morley, E. L., & Robert, D. (2018). Electric fields elicit ballooning in spiders. Current Biology, 28(14), 2324–2330.e2. DOI: 10.1016/j.cub.2018.05.057.

Morley, E. L., & Gorham, P. W. (2020). Evidence for nanocoulomb charges on spider ballooning silk. Physical Review E, 102, 012403. DOI: 10.1103/PhysRevE.102.012403.

Osterhage, D., et al. (2020). Multiple observations of bigfin squid (Magnapinna sp.) in the Great Australian Bight reveal distribution patterns, morphological characteristics, and rarely seen behaviour. PLOS ONE, 15(11), e0241066.

Quinn, T. P. (1997). Homing in Pacific salmon: mechanisms and ecological basis. Journal of Experimental Biology, 200, 2287–2294.

Stevens, M. (2013). Sensory Ecology, Behaviour, and Evolution. Oxford University Press.

Uexküll, J. von. (2010). A Foray into the Worlds of Animals and Humans: With a Theory of Meaning. University of Minnesota Press. Original work published 1934.

Walker, M. M., Dennis, T. E., & Kirschvink, J. L. (2002). The magnetic sense and its use in long-distance navigation by animals. Current Opinion in Neurobiology, 12(6), 735–744. DOI: 10.1016/S0959-4388(02)00389-6.


John Swygert

September 3, 2026

Copyright © John Swygert 2026

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THE INFORMATIONAL ECOSYSTEM:Overlapping Organismal Realities in a Shared Physical Environment

THE INFORMATIONAL ECOSYSTEM:

Overlapping Organismal Realities in a Shared Physical Environment

DOI: [to be assigned]

John Swygert

September 3, 2026


Abstract

An ecosystem is conventionally understood through interactions among organisms, energy, matter, resources, populations, and physical environmental conditions. Yet every ecological interaction also depends upon information. Organisms detect only selected portions of their physical environments, produce signals and environmental modifications detectable by other organisms, and respond according to biological architectures that differ across species, individuals, developmental states, and circumstances.

This paper proposes the informational ecosystem as a framework for representing an ecosystem as a superposition of partially overlapping organismal realities within a shared physical environment. The framework begins from a distinction established by comparative sensory biology: organisms occupying the same physical location need not possess access to the same environmental information. Ultraviolet reflectance may be available to one organism but absent from another's visual system. Weak electrical fields, magnetic-field properties, chemical gradients, substrate vibrations, hydrodynamic disturbances, acoustic signals, temperature differences, moisture gradients, molecular signals, and other environmental properties similarly differ in biological accessibility.

Let \(E\) represent a shared physical environment and let \(R_i=\Phi_i(E)\) represent the biologically accessible informational reality of organism \(i\). An ecosystem containing \(n\) organisms can then be represented not by a single perceptual environment but by a family of overlapping informational mappings:

\[ \mathcal{R}(E)=\{R_1,R_2,\ldots,R_n\}. \]

The intersections among these mappings identify shared informational domains. Their differences identify informational asymmetries. Their union approximates the portion of the environment accessible to the biological community as a whole, while remaining a subset of the complete physical environment.

This framework has implications for predator-prey interactions, pollination, symbiosis, parasitism, communication, camouflage, migration, microbial ecology, plant-fungal relationships, conservation, environmental disturbance, artificial intelligence, and the simulation of ecosystems. It also suggests a new experimental program: construct a common measured environment, model the informational access of multiple organisms within it, superimpose those models, and determine whether ecological interactions become more intelligible when analyzed as exchanges among overlapping biological realities.

An ecosystem is therefore not only a network through which matter and energy move.

It is also a network through which detectable differences become biological information.


1. Introduction

A forest contains trees, animals, fungi, microorganisms, soil, water, atmosphere, electromagnetic radiation, chemicals, sound, temperature gradients, pressure differences, mechanical forces, electrical activity, magnetic fields, and countless interactions among them.

Humans entering that forest perceive only a fraction of this structure.

A bird may detect visual and acoustic information unavailable or differently resolved by a human.

An insect may detect wavelengths and polarization patterns unavailable to unaided human vision.

A spider may receive detailed vibrational information through a web.

A plant may respond to light direction, photoperiod, water status, mechanical disturbance, neighboring organisms, herbivore damage, and chemical information.

A fungus may encounter the same location primarily through chemical, nutritional, mechanical, and moisture gradients.

A microorganism may inhabit a chemical landscape existing at spatial and temporal scales largely inaccessible to unaided human perception.

These organisms occupy one ecosystem.

They do not occupy one identical informational representation of that ecosystem.

This observation suggests that ecological systems can be analyzed not merely as collections of organisms interacting within a physical environment, but as collections of partially overlapping organismal realities.

The central proposition of this paper is:

An ecosystem contains one shared physical environment but many biologically accessible informational environments. Ecological interactions occur where those informational environments intersect, influence one another, or remain asymmetrical.


2. The Shared Physical Environment

Let the physical state of an ecosystem be represented as:

\[ E(x,t) \]

where \(x\) represents location and \(t\) represents time.

The environment contains numerous physical and chemical variables:

\[ E=\{L,A,C,T,P,M,F,V,Q,G,H,N,\ldots\} \]

where, for example:

  • \(L\) = electromagnetic radiation,

  • \(A\) = acoustic energy,

  • \(C\) = chemical composition,

  • \(T\) = temperature,

  • \(P\) = pressure,

  • \(M\) = magnetic-field properties,

  • \(F\) = fluid movement,

  • \(V\) = mechanical vibration,

  • \(Q\) = electrical properties,

  • \(G\) = gravitational information,

  • \(H\) = humidity or water availability,

  • \(N\) = nutrient distributions.

This environmental state exists independently of whether any particular organism detects every component.

No known organism has unrestricted access to \(E\).

Each organism instead interacts with a biologically filtered subset.


3. Organismal Reality Within the Ecosystem

For organism \(i\), define a biological accessibility transformation:

\[ \Phi_i. \]

Its biologically accessible environment is:

\[ R_i=\Phi_i(E). \]

Two organisms occupying the same physical coordinates may therefore satisfy:

\[ E_i=E_j \]

while:

\[ R_i\neq R_j. \]

This does not imply multiple physical universes.

It describes multiple biological mappings of one physical universe.

An ecosystem containing \(n\) organisms therefore contains:

\[ R_1,R_2,R_3,\ldots,R_n. \]

The complete set can be represented as:

\[ \mathcal{R}(E)=\{R_i\}_{i=1}^{n}. \]

This is the informational ecosystem.


4. Superposition Without Multiplying Reality

The term superposition is used here in a representational and comparative sense, not in the quantum-mechanical sense.

The organismal mappings can be placed upon a common physical coordinate system because they originate from the same environment.

For example:

\[ R_{\text{human}} \] \[ R_{\text{bee}} \] \[ R_{\text{spider}} \] \[ R_{\text{tree}} \] \[ R_{\text{fungus}} \] \[ R_{\text{bacterium}} \]

can be mapped onto the same square meter of forest.

The resulting layers expose information that is:

  • jointly accessible,

  • accessible to only one organism,

  • accessible to particular groups,

  • generated by one organism and detected by another,

  • or physically present but inaccessible to all organisms represented.

Thus superposition does not claim that realities physically coexist as separate worlds.

It is a method for comparing different biological access functions within the same world.


5. Informational Intersection

For organisms \(A\) and \(B\), consider:

\[ R_A\cap R_B. \]

This represents environmental information accessible to both organisms, subject to differences in resolution, threshold, timing, and biological interpretation.

The intersection can enable interaction.

A predator and prey may both detect movement.

Two animals may hear the same sound.

A pollinator and flowering plant may participate in an interaction involving signals generated by one and detected by the other.

Two microorganisms may respond to the same chemical environment.

However, shared detection does not imply identical representation.

Both organisms may detect a physical variable while responding to different ranges or aspects of it.

Therefore informational intersection should eventually be represented quantitatively rather than simply as present or absent.


6. Informational Asymmetry

Perhaps even more important is:

\[ R_A-R_B. \]

This represents information accessible to organism \(A\) but unavailable to organism \(B\).

Ecology contains enormous numbers of such asymmetries.

A predator may detect prey through a sensory channel unavailable to the prey.

A prey organism may detect the predator earlier through another channel.

A parasite may respond to chemical information produced unintentionally by a host.

A flower may generate ultraviolet patterns detectable by a pollinator but invisible to a human observer.

A shark may detect electrical information from an organism concealed from ordinary vision.

These asymmetries can determine survival.

An informational ecosystem is therefore not merely a network of communication.

It is also a network of unequal access.


7. Detection Is Not Necessarily Communication

A crucial distinction must be maintained between signals and cues.

An organism can generate information without having evolved to communicate it.

Footsteps produce vibration.

Metabolism produces heat.

Respiration alters chemical conditions.

Movement displaces water.

Electrical activity generates fields.

Waste products alter chemistry.

An organism may exploit these effects even when the source organism receives no benefit from producing them.

Thus:

\[ \text{information available to receiver} \]

does not imply:

\[ \text{intentional or evolved communication}. \]

The informational ecosystem includes both deliberate biological signaling and incidental detectable consequences of existence.


8. Predator and Prey

Predator-prey relationships provide a clear example.

Let:

\[ R_P \]

represent the predator's informational reality and:

\[ R_Y \]

the prey's.

Successful predation can depend partly upon:

\[ R_P(Y) \]

—the information about prey accessible to the predator.

Successful avoidance can depend upon:

\[ R_Y(P) \]

—the information about the predator accessible to the prey.

These quantities need not be symmetrical.

The ecological contest can therefore be viewed partly as:

\[ R_P(Y)\quad \text{versus}\quad R_Y(P). \]

Camouflage reduces information available through particular channels.

Silence reduces acoustic information.

Remaining down-current can alter chemical detection.

Motionlessness may reduce visual or mechanosensory information.

Burial can remove visual information while leaving electrical or chemical information detectable.

Predation therefore becomes partly a competition over informational visibility.


9. Camouflage as Informational Manipulation

Camouflage is usually discussed visually because human observers are highly visual.

But the broader framework reveals camouflage as a general informational phenomenon.

An organism can reduce detectability by altering:

  • visual contrast,

  • odor,

  • sound,

  • vibration,

  • thermal signature,

  • electrical signature,

  • movement,

  • chemical release,

  • or environmental disturbance.

The relevant question becomes:

Camouflaged from whom, and through which informational channel?

An organism may be visually concealed while remaining chemically obvious.

It may be acoustically quiet while producing detectable substrate vibrations.

It may be thermally conspicuous in visual darkness.

There is therefore no universal camouflage.

There is only camouflage relative to a detector.


10. Pollination as Informational Intersection

Pollination provides a different relationship.

Flowers can present combinations of:

  • color,

  • ultraviolet patterning,

  • shape,

  • odor,

  • nectar,

  • temperature,

  • spatial arrangement,

  • and timing.

Pollinators possess corresponding detection capabilities.

The interaction therefore depends upon an intersection between plant-generated environmental structure and pollinator-accessible information.

This can be represented conceptually as:

\[ I_{FP}=S_F\cap R_P \]

where:

  • \(S_F\) represents flower-generated information,

  • \(R_P\) represents pollinator-accessible reality,

  • \(I_{FP}\) represents the usable informational intersection.

A floral property physically present but biologically inaccessible to the pollinator cannot influence pollinator behavior through that channel.

Thus ecological signaling requires both production and accessibility.


11. Plants as Information-Producing Organisms

Plants do not merely receive environmental information.

They continuously modify informational environments.

Flowers alter spectral and chemical structure.

Roots alter soil chemistry.

Leaves alter light distribution.

Plants release volatile compounds.

Growth modifies mechanical environments.

Water uptake changes local conditions.

Herbivore damage can alter plant chemistry and subsequent interactions.

A plant is therefore simultaneously:

\[ \text{detector} + \text{processor} + \text{environmental modifier}. \]

The same is true, in different forms, for virtually every organism.


12. Fungal Networks

Fungi introduce distributed informational relationships.

A mycelial system can occupy large, heterogeneous spatial regions.

Different portions encounter different:

  • nutrients,

  • moisture,

  • chemicals,

  • organisms,

  • temperatures,

  • physical barriers,

  • and resource conditions.

The resulting growth and resource-allocation patterns can change the surrounding environment.

In mycorrhizal associations, fungal and plant biology become tightly coupled through exchanges of resources and signals.

The informational ecosystem therefore cannot always be represented as isolated organisms exchanging discrete messages.

Some relationships are continuous, distributed, and spatially interwoven.


13. Microbial Informational Ecosystems

At microbial scales, information can become extraordinarily dense.

Microorganisms respond to:

  • nutrients,

  • oxygen,

  • pH,

  • temperature,

  • toxins,

  • metabolites,

  • signaling molecules,

  • neighboring organisms,

  • surfaces,

  • flow,

  • and other environmental variables.

Quorum sensing demonstrates that chemical information associated with population density can alter collective biological behavior.

Biofilms further transform the local physical and chemical environment.

A microscopic environment that appears homogeneous to human observation may therefore contain numerous overlapping microbial informational landscapes.

Scale changes what constitutes an ecologically meaningful difference.


14. Symbiosis as Coupled Informational Reality

Symbiotic relationships create especially interesting overlaps.

Let organisms \(A\) and \(B\) interact repeatedly.

Each modifies the environment:

\[ E(t)\rightarrow E'(t) \]

and therefore modifies the other's accessible reality:

\[ R_B(t)=\Phi_B[E(t)] \]

becomes:

\[ R_B(t+1)=\Phi_B[E'(t)]. \]

Organism \(B\) then acts upon the altered environment, changing what becomes available to \(A\).

This produces a coupled informational loop:

\[ A\rightarrow E\rightarrow B\rightarrow E'\rightarrow A. \]

The relationship is therefore dynamic.

Organisms do not merely perceive an ecosystem.

They continuously rewrite portions of the informational ecosystem for one another.


15. Host and Pathogen

Host-pathogen relationships provide another form of informational conflict.

A pathogen must encounter, recognize, enter, exploit, or reproduce within a host environment.

The host simultaneously detects molecular evidence associated with invasion and initiates defensive responses.

The relevant informational spaces occur at molecular and cellular scales rather than at the ordinary human perceptual scale.

Thus the informational ecosystem extends inward.

An organism can itself constitute an ecosystem containing numerous informational relationships among host cells, microorganisms, parasites, viruses, and molecular signaling systems.

The distinction between environment and organism becomes scale-dependent.


16. Informational Reality Across Scale

One reason human intuition struggles with organismal reality is that biological information operates across enormous ranges of scale.

Relevant structures may occur across:

  • molecular,

  • cellular,

  • organismal,

  • local environmental,

  • landscape,

  • oceanic,

  • atmospheric,

  • and planetary scales.

Geomagnetic information may contribute to migration over enormous distances.

A chemical gradient may guide a microorganism across microscopic distances.

Both can function as navigational information.

The important variable is not absolute physical scale.

It is the relationship between environmental structure and biological detection.


17. Time as an Informational Dimension

Organisms also occupy different temporal realities.

Some information changes in milliseconds.

Other biologically relevant patterns unfold over:

  • minutes,

  • hours,

  • days,

  • seasons,

  • years,

  • or generations.

A human observer may fail to recognize plant movement because it occurs slowly relative to ordinary human attention.

A microorganism may respond to chemical fluctuations occurring at scales humans do not naturally monitor.

Migratory organisms respond to seasonal environmental change.

Circadian systems extract information from repeating planetary cycles.

Therefore organismal reality must be modeled in:

\[ (x,t) \]

rather than spatial coordinates alone.

Different organisms effectively sample the temporal environment at different resolutions.


18. Internal State Changes External Meaning

The same environmental information can have different biological significance depending upon internal state.

Food odor matters differently when an animal is satiated.

Water availability matters differently depending upon hydration.

Light can have different consequences depending upon circadian phase.

Chemical gradients can change significance according to metabolic requirements.

Reproductive state can alter responses to signals.

Thus:

\[ R_i=\Phi_i(E,S_i,H_i) \]

where:

  • \(E\) = environment,

  • \(S_i\) = internal state,

  • \(H_i\) = relevant biological history.

The informational ecosystem is therefore not static even when the physical environment remains temporarily unchanged.


19. The Biological Union

For an ecosystem containing \(n\) organisms, define the union:

\[ R_{\cup}=\bigcup_{i=1}^{n}R_i. \]

This represents, conceptually, the total portion of the environment biologically accessible to at least one organism included in the model.

This union may be enormously richer than the informational reality of any individual organism.

However:

\[ R_{\cup}\subseteq E. \]

There may be physically real information that none of the organisms detects.

Indeed, even if every known organism on Earth were included:

\[ R_{\text{life}} = \bigcup_{i=1}^{N}R_i, \]

there is no reason to assume:

\[ R_{\text{life}}=E. \]

This distinction is fundamental.

Life samples reality.

Life does not necessarily exhaust reality.


20. The Known Biological Envelope

The union of all demonstrated biological detection systems can be conceptualized as a known biological informational envelope.

Within it lie all physical variables currently known to be biologically detected or used by known life.

Outside it may lie physically measurable phenomena for which no biological detector is known.

The boundary itself becomes scientifically interesting.

We can ask:

Which dimensions of physical reality has evolution made biologically accessible somewhere on Earth?

And conversely:

Which measurable dimensions appear biologically unused?

These questions transform biodiversity into a survey of naturally evolved information-detection technologies.


21. Science Beyond the Biological Envelope

Human scientific instruments extend access beyond ordinary human biology and potentially beyond the entire known biological envelope.

Let:

\[ T(E) \]

represent technologically detected physical information.

Then scientific access can include:

\[ R_{\text{science}} = R_H\cup T(E). \]

Radio astronomy, particle physics, spectroscopy, microscopy, gravitational-wave detection, magnetic measurement, thermal imaging, and numerous other technologies reveal domains inaccessible to unaided humans.

Thus the complete comparison becomes:

\[ R_H \subset R_{\text{life}} \subseteq E \]

while technology provides additional mappings from \(E\) into human-accessible representation.

The precise set relationships must be established empirically rather than assumed, but the conceptual architecture is useful.


22. Organisms as Natural Detectors

Every sensory or environmental-response system can be viewed as an evolved detector.

The bee demonstrates one solution for extracting spectral information.

The shark demonstrates another for electrical information.

The salmon demonstrates biologically useful responses to chemical and geomagnetic information.

The spider demonstrates vibration-based information acquisition.

Plants demonstrate molecular and physiological environmental detection without animal nervous systems.

Microorganisms demonstrate navigation through chemical landscapes.

Fungi demonstrate distributed responses within heterogeneous environments.

Biodiversity therefore represents, among many other things, a vast natural library of physical-information detectors.


23. Ecosystem Information Networks

An informational ecosystem can be represented as a network.

Let organisms be nodes:

\[ O_1,O_2,\ldots,O_n. \]

Let an edge:

\[ O_i\rightarrow O_j \]

exist whenever activity by organism \(i\) produces or modifies information detectable by organism \(j\).

The edge can be classified by modality:

  • visual,

  • chemical,

  • acoustic,

  • electrical,

  • mechanical,

  • thermal,

  • hydrodynamic,

  • magnetic,

  • molecular,

  • or multimodal.

Edges can also be:

  • intentional signals,

  • incidental cues,

  • beneficial,

  • harmful,

  • mutualistic,

  • deceptive,

  • or neutral.

The ecosystem therefore becomes a dynamic, multilayer informational network superimposed upon conventional ecological networks of matter and energy.


24. Information Can Be Deceptive

Once organisms respond to detectable information, evolution can favor manipulation of those responses.

Mimicry provides an obvious example.

An organism can generate information resembling another organism or environmental feature.

The receiver acts upon the information because its biological detection and interpretation architecture maps that pattern to a particular response.

Therefore:

\[ \text{detectable information} \neq \text{accurate inference}. \]

The informational ecosystem contains not merely signals and cues, but misdirection.

This parallels human perception.

Biological systems act upon accessible information, not upon omniscient knowledge of physical reality.


25. Environmental Disturbance as Informational Disturbance

Human environmental modification can alter ecosystems informationally even when organisms remain physically present.

Artificial light changes nocturnal visual environments.

Anthropogenic noise changes acoustic environments.

Chemical pollution modifies chemical landscapes.

Electromagnetic infrastructure may alter environmental fields.

Turbidity changes optical conditions.

Habitat fragmentation changes spatial cues and navigation.

Climate change alters temperature gradients, seasonal timing, currents, and other environmental signals.

Therefore conservation should sometimes ask not only:

Has the habitat physically survived?

but:

Has the informational environment required by its organisms survived?

A habitat can remain geographically present while becoming informationally degraded.


26. Informational Pollution

This suggests a broader category: informational pollution.

Informational pollution occurs when environmental modification interferes with biologically important information acquisition or produces misleading signals.

Examples can include:

  • artificial light obscuring natural light cues,

  • noise masking communication,

  • chemicals interfering with olfactory environments,

  • altered water conditions changing signal propagation,

  • human structures disrupting navigational cues.

The concept unifies environmental effects that are otherwise treated separately.

The common mechanism is:

\[ \text{environmental modification} \rightarrow \text{altered accessible information} \rightarrow \text{altered biological behavior}. \]


27. Simulating an Informational Ecosystem

The framework can be tested computationally.

First construct a shared physical environment:

\[ E(x,t). \]

Then construct organismal mappings:

\[ R_1=\Phi_1(E) \] \[ R_2=\Phi_2(E) \] \[ \vdots \] \[ R_n=\Phi_n(E). \]

Then simulate interactions among organisms.

Each organism or artificial agent receives only the information available through its own model.

No organism receives omniscient access to \(E\).

The simulation records:

  • detected information,

  • undetected information,

  • behavioral decisions,

  • signaling,

  • environmental modifications,

  • interactions,

  • survival,

  • movement,

  • reproduction,

  • and ecological consequences.

This creates an experimentally manipulable informational ecosystem.


28. Informational Ablation

Individual channels can then be removed.

For example:

\[ R_i^{(-M)} \]

could represent an organism model deprived of magnetic information.

Similarly:

\[ R_i^{(-C)} \]

could remove a chemical channel.

Researchers could ask whether ecological interactions change.

Does migration deteriorate?

Does predation success change?

Does pollination decline?

Does habitat selection change?

Does symbiosis destabilize?

The ecosystem-level consequences of sensory loss may reveal dependencies invisible when organisms are studied individually.


29. Informational Addition

The inverse experiment is equally interesting.

An organism model can be given access to a channel it does not biologically possess.

For example:

\[ R_i^{(+X)}. \]

Researchers could then ask:

What would this organism be capable of if this dimension of physical information became available to it?

This is not a claim about biological evolution.

It is a counterfactual experiment concerning informational constraint.

Such experiments could illuminate why particular sensory architectures confer advantages in particular ecological niches.


30. Artificial Intelligence Within the Informational Ecosystem

Artificial agents provide a powerful experimental tool because their informational access can be precisely controlled.

One agent can receive:

\[ R_A. \]

Another receives:

\[ R_B. \]

A third receives a novel combination:

\[ R_C=R_A\cup R_B. \]

The agents can then compete, cooperate, forage, migrate, or survive within the same environment.

This allows researchers to test whether informational differences alone can generate ecological advantages or behavioral patterns.

It also provides a way to investigate the value of sensory combinations that do not occur naturally.


31. The Human Observer Must Also Be a Layer

Humans should not occupy a privileged position within the informational ecosystem model.

The human observer should be represented as:

\[ R_H=\Phi_H(E). \]

A separate scientific instrumentation layer can then reveal:

\[ T(E). \]

This distinction prevents human perception from being confused with the underlying simulation.

The researcher can compare:

\[ R_H \]

with:

\[ R_i \]

and with:

\[ E. \]

Humanity thereby becomes one organismal perspective among many while retaining the ability to construct technological translations of information outside ordinary human access.


32. A Square Meter of Forest

A practical experimental unit could be remarkably small.

Consider one square meter of forest floor.

Measure:

  • light,

  • temperature,

  • humidity,

  • soil moisture,

  • chemical gradients,

  • vibration,

  • acoustic conditions,

  • airflow,

  • electrical conditions,

  • magnetic conditions,

  • nutrient distributions,

  • and biological activity.

Then model the informational realities of:

  • a human,

  • an insect,

  • a spider,

  • a plant,

  • a fungus,

  • a nematode,

  • and several microorganisms.

The physical coordinate domain remains constant.

The organismal mappings differ.

Superimpose them.

The result would not merely show what lives there.

It would show which portions of that place exist as biologically usable information for each form of life.

That is a fundamentally different map of an ecosystem.


33. From Maps of Species to Maps of Perspective

Traditional ecological maps commonly represent:

  • species distributions,

  • habitat types,

  • vegetation,

  • temperature,

  • precipitation,

  • resources,

  • and physical geography.

An informational ecosystem map would add:

  • detectable chemical fields,

  • relevant spectral information,

  • acoustic environments,

  • vibration networks,

  • electrical fields,

  • hydrodynamic cues,

  • navigational information,

  • organism-generated signals,

  • and sensory accessibility.

The resulting map would be observer-indexed.

Instead of asking:

What is present here?

it would also ask:

Present to whom?


34. Implications for Ecology

The informational ecosystem framework does not replace conventional ecology.

Energy remains essential.

Matter remains essential.

Population dynamics remain essential.

Evolution remains essential.

Physical habitat remains essential.

The proposed framework adds another layer:

\[ \text{Matter} + \text{Energy} + \text{Information}. \]

Organisms require matter and energy to survive.

But they require information to locate resources, avoid threats, reproduce, regulate internal conditions, interact with other organisms, and navigate changing environments.

Information is therefore not an ornamental description of ecology.

It participates directly in ecological function.


35. Implications for Evolution

Evolution acts upon organisms whose survival depends partly upon detecting useful environmental differences.

Sensory systems can therefore evolve as solutions to informational problems.

Likewise, signaling systems can evolve because receivers respond to particular information.

Camouflage evolves because detectors can be defeated.

Mimicry evolves because informational classifications can be exploited.

Predators evolve improved detection.

Prey evolve improved concealment or warning systems.

The informational ecosystem is therefore itself evolutionary.

The mappings:

\[ \Phi_i \]

change across generations.

Life evolves not only within physical environments.

It evolves ways of accessing those environments.


36. Implications for Consciousness

The informational ecosystem framework does not require consciousness.

A bacterium can participate.

A plant can participate.

A fungus can participate.

An animal can participate.

A human can participate.

The relevant criterion is biologically consequential information detection and response.

Nevertheless, consciousness research may benefit from the framework because conscious organisms exist inside informational architectures shaped by these ecological relationships.

If consciousness depends in part upon integrated biological information, then understanding the information available to an organism provides constraints upon what could enter its experienced world.

But the distinction must remain:

\[ \text{informational reality} \neq \text{phenomenal consciousness}. \]

The former can be studied without presupposing the latter.


37. A Research Program

The informational ecosystem hypothesis suggests a concrete research program.

Select a bounded environment.

Measure its relevant physical variables.

Identify representative organisms.

Characterize their demonstrated detection systems.

Construct organism-specific informational mappings.

Track real behavior.

Construct simulated agents restricted to the same information.

Compare simulated and biological behavior.

Then manipulate:

  • sensory channels,

  • signal strength,

  • environmental noise,

  • cue conflict,

  • internal state,

  • and ecological relationships.

The result would be a controlled test of whether ecological behavior becomes more predictable when organisms are modeled according to the information actually available to them rather than according to an omniscient representation of the environment.


38. The Informational Ecosystem Hypothesis

The central hypothesis of this paper can be stated formally:

Ecological interactions can be more completely modeled by representing each organism as operating within a biologically constrained informational mapping of a shared physical environment and by explicitly modeling the intersections, asymmetries, transmissions, modifications, and conflicts among those mappings.

This hypothesis generates empirical predictions.

Models incorporating realistic informational constraints should, under appropriate circumstances, outperform equivalent models that provide agents with unrestricted environmental information.

Removing biologically important information channels should produce predictable behavioral and ecological disruptions.

Restoring those channels should restore corresponding performance.

Environmental disturbances that alter relevant information should produce effects consistent with field observations.

These propositions are testable.


39. Conclusion

An ecosystem is not experienced uniformly by the organisms inhabiting it.

The physical forest is shared.

The informational forest is plural.

The physical ocean is shared.

The informational ocean is plural.

The physical soil is shared.

The informational soil is plural.

A human, bee, spider, plant, fungus, bacterium, shark, salmon, bat, and every other organism interacts with physical reality through biological constraints that determine which environmental differences become accessible information.

These mappings can be represented as:

\[ R_i=\Phi_i(E). \]

The ecosystem then becomes:

\[ \mathcal{R}(E)=\{R_1,R_2,\ldots,R_n\}. \]

Its informational overlaps are:

\[ R_i\cap R_j. \]

Its asymmetries include:

\[ R_i-R_j. \]

Its biologically accessible union is:

\[ R_{\cup}=\bigcup_{i=1}^{n}R_i. \]

Yet even that union need not equal:

\[ E. \]

There may always remain physical information outside the biological access of the organisms being considered.

This distinction changes the way an ecosystem can be conceptualized.

A predator does not merely encounter prey.

It encounters information produced by prey.

Prey does not merely encounter a predator.

It encounters whatever information about that predator its biology permits it to detect.

A pollinator does not encounter an abstract flower.

It encounters a particular subset of the flower's physical properties.

A plant does not inhabit generic soil.

Its biology responds to particular gradients and signals within that soil.

A microorganism does not inhabit an empty droplet.

It inhabits a structured chemical and physical landscape.

A fungus does not merely occupy space.

It grows through a distributed field of biologically meaningful differences.

These realities overlap.

They interact.

They conceal.

They reveal.

They deceive.

They cooperate.

They compete.

And organisms continuously modify them for one another.

Ecology can therefore be understood not only as the study of organisms exchanging matter and energy within environments, but also as the study of organisms detecting, producing, transforming, obscuring, and exploiting information within those environments.

The proposed informational ecosystem does not replace the physical ecosystem.

It exposes another dimension of it.

There is one physical environment.

There are many biological mappings of that environment.

Their intersections help make ecological relationships possible.

Their differences create informational advantages and disadvantages.

Their union reveals more of the environment than any single organism can access.

And their superposition offers a new way of seeing life:

not merely as organisms occupying the same world, but as organisms occupying overlapping windows onto the same reality.


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John Swygert

September 3, 2026

Copyright © John Swygert 2026

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