Capture & check
Synchronize time, coordinates, calibration and conditions. Find unusable data while still in the field.
Drones × multisensor observations × AI.
Move from finding wildlife to understanding it.
Design better surveys for animals and researchers.

Counting is just the beginning. Where do animals live, and how do they use their world? Let’s explore what the view from above can tell us.
Individuals, behaviour and habitat. Connect the ecological question to the right sensor—and its limits.
A detection count is not a population estimate. Combine thermal and visible imagery, then check missed animals and duplicates.
Observe without moving closer. Connect zoom imagery, transmitter signals and time-aligned behavioural records.
Read the places animals inhabit. Connect terrain, vegetation structure and seasonal change to habitat use.
Return safely, deliver usable observations and make next year’s comparison possible. Design the whole survey.
Read the field guide ↗Include repeat surveys, human verification and storage. Compare total cost at the required level of ecological quality.
Read the field guide ↗Keep observations, estimates and evidence distinct but connected. Simple to interpret, detailed enough to reproduce.
Read the field guide ↗Methods, field practice and implementation designs. Every guide offers a route back to its evidence.
Reducing missed animals, field exposure and cost starts with the survey design, not the aircraft specification.
Heat can reveal candidates; shape and colour can help identify them. Their failure modes remain different.
A model count needs detection probability, duplicate control, an area denominator and uncertainty.
Connect location, visible behaviour and physiology with synchronized records and explicit uncertainty.
Habitat is more than green cover: height, gaps, water, forage and refuge shape how animals use space.
Build a species- and context-specific flight protocol instead of claiming a universally safe altitude.
Thrust, ground sampling distance, blur and endurance connect aircraft choices to usable evidence.
Battery rotation, data integrity and recovery decisions determine throughput alongside flying.
Connect ingestion, detection, review and estimation with reproducible records.
Test transfer across sites, seasons, sensors and target sizes instead of relying on one accuracy score.
Place computation according to latency, power, connectivity and verification needs.
Compare complete survey costs at an equivalent ecological endpoint and uncertainty level.
Allocate airspace, energy, communication and wildlife exposure before adding more aircraft.
Separate automation capabilities from Japan-specific operating categories, permissions and animal welfare.
Separate surveys, flights, assets, detections, observations and estimates so tools can change without losing provenance.
Precise locations can support research and expose vulnerable wildlife. Design access and generalization together.
Follow the shift from obtaining aerial images to validating ecological measurements and operational value.
Work back from the research outcome and connect responsibilities across acquisition, analysis, validation and operations.
Behaviour, physiological response and habituation answer different questions. Read two bear studies without turning them into universal flight rules.
Controlled references and independent field checks answer different questions about counting performance.
No results. Try a shorter or different search term.
A lack of visible escape does not establish a lack of stress. Plan from species, breeding context, habitat, aircraft and observed responses.
Read the welfare protocol ↗Connect capture, AI, validation and reporting. Put quality gates in place before claiming full automation.
Synchronize time, coordinates, calibration and conditions. Find unusable data while still in the field.
Record candidates without connectivity. Retain raw evidence and timestamps for later omission audits.
Align, tile, detect and deduplicate. Track processing versions and failures.
Sample negatives as well as low-confidence detections. Measure omissions and false positives.
Return to the sampling design. Account for detection probability and uncertainty.
Deliver comparable maps, time series and coverage, with a path back to the evidence.
This is an implementation design guide. This website does not control aircraft or run image inference.
What was studied, where and how? Follow original sources, review depth and limitations.
The target is 30 relevant sources per country. Comparable public national readership data is unavailable, so this is not a most-read ranking. Actual coverage and shortfalls are shown. Editorial policy & coverage ↗
Loading research records…
Replace assumptions and check readiness. Your inputs are not sent to a server.
An illustrative comparison for equivalent research outputs. Defaults are fictional, not market prices or predicted returns. Amounts are in JPY.
Excludes tax, interest, residual value and grants. The repeat-survey rate scales the entire variable survey cost. Ecological accuracy and animal burden may differ.
Baseline = surveys × (baseline hours × rate + travel). Drone = capex / allocation years + maintenance + surveys × [(flight + review hours) × rate + travel + AI/storage] × (1 + repeat rate). Simple payback = capex / annual cash savings before capex allocation.
A preparation memo for researchers, operators and site managers. This does not replace permissions or animal ethics review.
Checks live only on this page. Use export to keep a local copy.
Explore ground sampling distance and motion blur for an ideal nadir camera above flat ground. Starting values are illustrative, not specifications for a particular aircraft.
This is a geometry model. It does not determine legal or welfare-safe altitude, or whether an animal can be identified. Use the actual focal length, not a 35 mm equivalent.
GSD = H × S / (f × W); footprint width = H × S / f; motion blur (px) = v × t / GSD.
H: height in m; S: sensor width in mm; f: focal length in mm; W: image width in px; v: ground speed in m/s; t: exposure in seconds. Terrain, tilt, distortion, vibration, animal motion and rolling shutter are excluded. Effective thermal resolution and identification performance require separate validation.

What we know, what we don’t, and how we can find out. That boundary is where the next good survey begins.