Collaboration

Notes on representing collaboration and co-design with nonhuman beings.

Types of Agents

Design can collaborate with more than species. For more, see: Biological Individuality

A species name helps locate a being within taxonomy and conservation systems. However, actual design relations often occur at other levels.

For example:

  • A single animal may use or reject an artificial habitat.
  • A local population may depend on movement corridors.
  • A colony may build, filter or stabilise a substrate.
  • A holobiont may survive through microbial relations that remain invisible at the species level.
  • A guild may provide a service such as pollination, decomposition or hollow use.
  • A habitat system may support many taxa without belonging to one species.
  • An ecosystem may act through linked flows of water, nutrients, shade, shelter, disturbance and reproduction.

Collaboration Networks

The design relation matters as much as the taxonomic position.

IndividualSignal (action or trace)ContributionIntervention
Anguillid eelsMigration routes, passage refusal, burrowing tracesReveal connectivity gaps, redistribute nutrients, reshape substrateRedesign fish passages, protect migratory corridors, monitor eel-led indicators
Australian flat oyster (Ostrea angasi)Settlement density, recruit survival, reef accretionBuild reef substrate, filter water, create habitat for other speciesIterative redesign of reef modules, placement, and surface complexity
Blue-banded bee (Amegilla cingulata)Visitation and nesting activityPollination and persistence in urban ecologiesReconfigurable habitat structures and floral resource planning
Arboreal termites (Nasutitermes walkeri)Nest geometry and material performanceDemonstrate lightweight, thermally stable habitat construction logicsBiomimetic design rules for fabricated habitat structures
Oyster mushroom (Pleurotus ostreatus)Mycelial growth pattern, binding quality, decay dynamicsProvide bio-based structural material and decomposition capacityGrow mycelium-bound prosthetic nests, tune substrate and curing protocols
Large old trees (for example Eucalyptus, ash, oak)Hollow formation, canopy form, branch architectureProvide long-term shelter, microclimate buffering, and habitat scaffoldsLaser-scan and model host trees, graft prosthetic hollows where needed
Cavity-nesting birds (for example tits, sparrows, owls)Occupancy, nest modification, reproductive successEvaluate habitat suitability and set practical design criteriaCompare nest types, adjust geometry and thermal performance across iterations
Moss communities (bryophytes)Surface colonisation, moisture retention, particulate captureRegulate microclimate, support near-surface biodiversityDesign porous substrates and near-surface ecologies for establishment at scale

Other Possible Contributions (Services)

  • Seed dispersal and assisted regeneration.
  • Pest suppression and trophic regulation.
  • Water filtration and nutrient retention.
  • Sediment stabilisation and shoreline protection.
  • Carbon storage and long-term biomass accumulation.
  • Heat buffering and urban cooling.
  • Hydrological moderation (infiltration, interception, flow delay).
  • Soil formation and porosity improvement.
  • Biogeochemical cycling (nitrogen, phosphorus, silica).
  • Bioindication of disturbance, toxicity, drought, and disease.
  • Material innovation through growth-based fabrication.
  • Cultural and pedagogical services (place attachment, multispecies learning).

Possible Interventions for Future Mapping

  • Habitat corridor repair across fragmented sites.
  • Seasonal resource mosaics (flowers, shelter, moisture, substrate).
  • Multi-species shelter gradients instead of single-species units.
  • Substrate palettes tuned to colonisation succession.
  • Adaptive placement protocols based on occupancy feedback.
  • Disturbance refugia and microclimate patches.
  • Co-monitoring protocols combining sensor and field observation traces.
  • Exclusion and access controls to reduce harmful overlap.
  • Managed decomposition zones for nutrient cycling and habitat.
  • Policy and maintenance triggers linked to nonhuman signals.
  • Co-design governance rules with explicit nonhuman thresholds.

Named Frameworks for Tables, Matrices, Diagrams, and Categories

FrameworkPurposeIntended use by authors and current usersOutput form and typical artefactPossible future splits or investigation lines
Common International Classification of Ecosystem Services (CICES) v5.11Standardise contribution categoriesEnvironmental accounting and policy teams use it to classify ecosystem services consistently across assessmentsCategory schema: hierarchical classification tableSplit by biome and urban vs regional contexts; test category fit for multispecies design cases
Intergovernmental Science-Policy Platform on Biodiversity and Ecosystem Services (IPBES) Nature's Contributions to People (NCP)2Capture plural values of natureIPBES authors, assessment panels, and biodiversity planners use it to include diverse value systems in evaluationsCategory schema: value-category matrixSplit by stakeholder groups; compare Indigenous-led and policy-led value frames
Driver-Pressure-State-Impact-Response (DPSIR)3Structure intervention logicEnvironmental agencies and indicator programmes use it to link pressures, states, impacts, and policy responsesCausal framework: chain table or flow diagramAdd temporal scales (event, seasonal, decadal); test alternative response pathways
Rights of Nature and legal personhood for nature4Establish legal standing for ecosystems or species collectivesLegislatures, courts, and guardianship bodies use it to represent rivers, forests, and ecosystems as rights-holdersGovernance and regulation framework: rights-holder registry and guardian mandate modelCompare guardian designs; track enforceability, remedies, and ecological outcomes across jurisdictions
Ecological Network Frameworks5Represent interaction structureEcologists use it to model trophic and non-trophic interactions and infer stability and functionInteraction taxonomy: interaction matrixSeparate trophic and facilitation layers; investigate seasonal rewiring of interactions
Leopold Matrix6Score intervention effects systematicallyEnvironmental impact assessors use it to score project actions against environmental componentsImpact matrix: action by component scoring gridSplit direct and indirect effects; add confidence and reversibility scoring dimensions
Ecosystem Engineering Typology7, 8Distinguish mechanism of environmental changeEcology researchers use it to classify biotic physical modifications and evaluate ecosystem-level consequencesMechanism categorisation: autogenic vs allogenic matrixSplit engineering intensity classes; compare engineered habitat longevity and spillover effects

Templates to Reuse

TemplateFramework baseMinimal columns or fields
Contributor x Service matrixCICES + NCPCollaborator, service class, evidence signal, confidence, scale
Intervention x Impact matrixLeopold Matrix + DPSIRIntervention, pressure change, state variable, impact, response metric
Socio-ecological adjacency matrixSocial-Ecological Network AnalysisNode A, relation type, Node B, strength, evidence source
Niche construction coding tableNCT + ecosystem engineeringActor, modification, inceptive/counteractive, autogenic/allogenic, inheritance pathway
Site suitability scoring tableGIS-MCDASite, criterion, weight, score, weighted total, decision

Examples

Socio-ecological systems.9

"Panarchy" is the term we use to describe a concept that explains the evolving nature of complex adaptive systems. Panarchy is the hierarchical structure in which systems of nature (for example, forests, grasslands, lakes, rivers, and seas), and humans (for example, structures of governance, settlements, and cultures), as well as combined human-nature systems (for example, agencies that control natural resource use) and social-ecological systems (for in- stance, co-evolved systems of management), are interlinked in never-ending adaptive cycles of growth, accumulation, restructuring, and renewal.10

Legal rights for rivers.4

Leopold Matrix for scoring environmental impact.6

Data Sources

  • Open Tree of Life: synthetic phylogeny, taxonomy alignment, lineage context. Has API and supports a variety of visualisation tools.
  • NCBI Taxonomy: curated taxon identifiers, names, and hierarchy.
  • GBIF: species pages, occurrence records, distribution evidence.
  • Catalogue of Life: accepted names, synonyms, and taxonomic backbone.

Visualisation Options

Tree of Life (Cladogram or Radial Tree)

Shows where collaborators sit across evolutionary and taxonomic relationships.

Useful for:

  • demonstrating taxonomic diversity
  • revealing representation across major branches of life
  • situating collaborators within broader evolutionary history

Examples:

  • eel
  • fairywren
  • oyster
  • eucalyptus
  • fungus
  • soil bacteria

Levels of Individuality Diagram

Shows the biological scale at which collaboration occurs.

Useful for:

  • moving beyond species-centric thinking
  • identifying meaningful units of action and response
  • comparing collaborations across scales

Levels:

  • cell
  • organism
  • colony
  • symbiotic association
  • holobiont
  • population
  • species
  • guild
  • community
  • ecosystem
  • biome
  • biosphere
  • earth system and solar-terrestrial context

Examples:

  • organism: individual eel
  • colony: oyster reef
  • holobiont: tree and microbiome
  • community: soil microbiome
  • ecosystem: wetland

Bipartite Collaboration Network

Links collaborators to projects, actions or design interventions.

Useful for:

  • revealing which collaborators participate in multiple projects
  • identifying shared ecological functions
  • mapping interactions rather than taxonomy

Examples:

  • eel population → fish passage design
  • oyster colony → reef restoration
  • hollow-using guild → artificial habitat design

Matrix or Heatmap

Shows the presence and strength of relationships.

Useful for:

  • comparing many collaborators simultaneously
  • revealing clusters and gaps
  • supporting detailed analysis

Rows:

  • collaborators

Columns:

  • projects
  • habitats
  • ecological functions
  • design relations

Multilayer Network

Combines taxonomy, biological individuality and design relations.

Useful for:

  • representing collaboration as a socio-ecological system
  • linking evolutionary, ecological and project data
  • understanding nonhuman participation at multiple scales

Layers:

  • taxonomic identity
  • biological individuality
  • ecological functions
  • projects
  • sites

Notes


Footnotes

  1. Haines-Young, Roy H. Common International Classification of Ecosystem Services: Guidance on the Application of the Revised Structure. 5.2. Barton in Fabis: European Environment Agency (EEA), 2023. https://cices.eu/resources/.˄

  2. Díaz, Sandra, Unai Pascual, Marie Stenseke, Berta Martín-López, Robert T. Watson, Zsolt Molnár, Rosemary Hill, Kai M. A. Chan, Ivar A. Baste, and Kate A. Brauman. “Assessing Nature’s Contributions to People.” Science 359, no. 6373 (2018): 270–72. https://doi.org/10.1126/science.aap8826.˄

  3. Carnohan, Shane A., Xenia Trier, Suxia Liu, Lauge P. W. Clausen, Jai K. Clifford-Holmes, Steffen F. Hansen, Lorenzo Benini, and Ursula S. McKnight. “Next Generation Application of DPSIR for Sustainable Policy Implementation.” Current Research in Environmental Sustainability 5 (2023): 100201. https://doi.org/10.1016/j.crsust.2022.100201. (Used by the European Environment Agency and in United States Environmental Protection Agency Office of Research and Development (ORD) research programmes.)˄

  4. O’Donnell, Erin L., and Julia Talbot-Jones. “Creating Legal Rights for Rivers: Lessons from Australia, New Zealand, and India.” Ecology and Society 23, no. 1 (2018): art7. https://doi.org/10.5751/es-09854-230107.˄

  5. Ings, Thomas C., José M. Montoya, Jordi Bascompte, Nico Blüthgen, Lee Brown, Carsten F. Dormann, François Edwards, et al. “Review: Ecological Networks—beyond Food Webs.” Journal of Animal Ecology 78, no. 1 (2009): 253–69. https://doi.org/10.1111/j.1365-2656.2008.01460.x.˄

  6. Leopold, Luna Bergere, Frank Eldridge Clarke, Bruce B. Hanshaw, and James R. Balsley. A Procedure for Evaluating Environmental Impact. Circular No. 645. US Geological Survey, 1971. https://doi.org/10.3133/cir645.˄

  7. Jones, Clive G., John H. Lawton, and Moshe Shachak. “Organisms as Ecosystem Engineers.” In Ecosystem Management: Selected Readings, edited by Fred B. Samson and Fritz L. Knopf, 130–47. New York: Springer, 1996.˄

  8. Jones, Clive G., John H. Lawton, and Moshe Shachak. “Positive and Negative Effects of Organisms as Physical Ecosystem Engineers.” Ecology 78, no. 7 (1997): 1946–57. https://doi.org/10.1890/0012-9658(1997)078%255B1946:PANEOO%255D2.0.CO;2.˄

  9. Ostrom, Elinor. “A General Framework for Analyzing Sustainability of Social-Ecological Systems.” Science 325, no. 5939 (2009): 419–22. https://doi.org/10.1126/science.1172133.˄

  10. Holling, C. S. “Understanding the Complexity of Economic, Ecological, and Social Systems.” Ecosystems 4, no. 5 (2001): 390–405. https://doi.org/10.1007/s10021-001-0101-5.˄