A Map Feature Is Not a Deer: Rank the Evidence
A bench on lidar is ground, a wind arrow is a forecast, and a dark patch on an aerial could be canopy, shadow or water. None of them is a deer. This guide sets out a six-rung evidence ladder that ranks what you hold, from an app drawing up to individually identified animals, and shows which methods (a sign walk, an observation log, a camera survey) can move a spot up it.
IDetection
A 2002 paper in Ecology by MacKenzie and colleagues, indexed on the USGS publications page, opens with a plain point: failing to detect a species at a site does not mean it is absent unless the probability of detection is 1. Their data were toads and spring peepers at 32 Maryland wetlands, not whitetails. For American toads they estimated occupancy at 0.49, a 44 percent increase over the share of sites where the animal was actually observed. Do not carry those numbers over to deer. The logic does transfer: a quiet sit, an empty card or a clean trail on Tuesday leaves the question open.
The reverse also holds, because one detection is not a count. University of Missouri (MU) Extension's guide to observational data (G9482, reviewed November 2022) says observations cannot be used to determine actual deer abundance, though they can show trends over time. It also warns that observed sex ratios can be biased toward does and young bucks, because mature bucks tend to be more nocturnal and are less likely to be seen. If your proof is what walked past a stand at last light, you sampled a narrow window.
Scale matters as well. Wildlife Illinois reports average home ranges of 0.44 square miles for does in agricultural areas of Illinois and 0.17 square miles for does in forest preserves near Chicago, and says bucks tend to have larger ranges. A pin is a point, and a home range is an area, so one detection at one point samples a small part of it.
IIThe ladder
The ladder is a working method from FDR's desk, not a published census. Give each spot one rung, the highest you can defend, and do not skip any.
| Rung | What you hold | What it supports | What it cannot support |
|---|---|---|---|
| 0. Drawing | A funnel, cover zone, score or marker on an app | A place to look | Use, timing or a deer |
| 1. Capability | Habitat that could meet a need (cover, food, water, space), read from a map or image | Why the spot made your list | That a deer chose it |
| 2. Current condition | A recent image or a walk shows the cut, crop, pond or thicket still exists | The feature is real now | Occupancy |
| 3. Sign | Tracks, pellets, beds, browse lines, rubs, scrapes | Deer used the ground at some time | Which deer, how often, or in daylight |
| 4. Repeated sign | The same kind of sign on several dates, such as a trail or rub line you check again | A pattern worth hunting | A count |
| 5. Identified animals | Individual bucks recognized on camera, or every sighting classified with hours logged | Herd ratios from either method; a density estimate only from a camera survey with real identification | That the animal will be there at shooting light; actual abundance from a log alone |
- A wind arrow cannot climb it. Treat the forecast as a scent-risk screen for hunting conditions, because it says nothing about where a deer's nose will be.
- A terrain feature such as a bench or saddle stops at rung 1 by itself. It is ground, and ground says where deer could travel.
- One clear camera photo shows that animal at that place and time. A herd estimate needs repeated sampling and identification work that a single photo does not supply.
- Do not average rungs. Calling a spot "mostly a 4" is how people talk themselves into hunting a 0.
Rung 3 rests on published sign lists. Wildlife Illinois lists heart-shaped tracks, dark cylindrical pellets, deer beds, browse lines, rubs and scrapes as the usual signs. Purdue's guide to assessing land for wildlife says a biologist checks whether a species is on a property through tracks, observations, nests and evidence of browsing or feeding, and treats a more detailed census as a separate step.
IIIClimbing the ladder
The notebook is the method that travels furthest. G9482 needs a pencil, paper and binoculars. You count every deer you see on each outing, classify each as buck, doe, fawn or unknown, and record your hours. MU's rule is blunt: "Do not guess on the classification of a deer." Its sample data show 93 deer over 56 observation hours, a sighting rate of 1.67 deer per hour. That rate measures your effort at your stands, and it does not count the deer on the property. MU also says consistency is extremely important, so collect the data the same way and in the same period every year or the comparison falls apart.
The camera survey in MU's G9481 is a real method with real constraints. It divides the property into a grid with, usually, one camera per 100 acres, runs in late August, sets out about 50 pounds of corn about a week before the survey starts and photographs for 10 to 14 days. You then identify each individual buck from antler and body characteristics and derive doe and fawn numbers from ratios. In MU's worked example, 8 identified bucks and the observed ratios produce a population of 44 on 1,000 acres. The estimate hangs on the unique-buck count, which is why that identification step has to be real.
Bait is what makes the camera method work, and baiting rules vary. G9481 records that as of Sept. 30, 2012, consumable attractants were prohibited in Missouri's Chronic Wasting Disease (CWD) Zone counties, and it sends those properties to the observational method. That is historical extension text and not a current rulebook. Illinois has its own rule, 17 Ill. Adm. Code 635.40: "It shall be illegal to make available food, salt, mineral blocks or other products for ingestion by wild deer" where deer are present, with listed exemptions that include standing crops planted as food plots. The JCAR site that hosts the code says its copy is not the official text. Check current rules with your state agency before you put out bait for any reason.
IVWhere map layers stop
| Layer | What it actually is | Highest rung it reaches on its own |
|---|---|---|
| App drawing (funnel, cover zone, score) | A model's output | 0 |
| Terrain (lidar or contours) | The ground surface | 1 |
| Aerial or satellite image | Objects on one flight date | 1, and 2 only when the image is recent and you check it |
| Wind forecast | A forecast for a point | Off the ladder; a scent-risk screen only |
| County harvest or crash statistics | Counts at county scale | Context for where to look, not evidence about a spot |
If you cannot point to the row you are using, you are on the first row.
Each layer has an FDR guide that goes further. For terrain, Reading a Bench, Saddle, and Draw on a Topo Map turns each feature into a zone and not a pin. For wind, When to Trust Your Wind Forecast covers why the arrow is weakest on calm, clear, cold mornings. For scores, Deer Movement Scores vs. What the Collar Studies Support sorts what a hunting day can and cannot be scored on. For county proxies, Why Deer-Crash Maps Lie shows how a collision count ends up indexing traffic and not deer.
VNext step
Pick a spot you plan to hunt and write its rung in four words, such as "rung 2, cut confirmed." If you cannot defend a 3, do not hunt the spot as if it were a 5. When the rung is 0 or 1, the next action on ground you own or have permission to enter is a sign walk, a notebook or a camera set within your state's rules, and a dawn sit in the middle of the feature can wait.
See what Scout maps. Its features page describes county harvest trends drawn from Illinois DNR records for 2005 through 2024, which is county-scale context for choosing where to look, and its footer calls FDR's rankings, indexes and scores "estimates, not guarantees of hunting outcomes."
- Aerial imagery, terrain, and parcel layers describe the ground on the date they were captured or recorded. They are not surveys or legal boundaries.
- Nothing here guarantees deer activity or hunting success. Confirm seasons, regulations, and permission before you hunt.
Fully Drawn Research is an independent data analysis desk, not affiliated with the Illinois Department of Natural Resources, the Illinois Department of Transportation, or any mapping or outfitting provider. FDR maps give context from public imagery, terrain, and parcel records; they do not predict deer activity or replace a field check.