- Date
- 2026-08-02
- Eras
- Modern era
- Concepts
- forestswetlandsenvironmentconservationgeologyland-survey
- Within
- Beaver Island archipelago
Summary
This is a dated snapshot of Michigan DNR’s public Michigan Forest Inventory System stand-covertype layer, clipped to the project’s seven named island frames. The service describes a stand as a relatively homogeneous polygon whose attributes may include canopy composition, age, age structure, basal area, origin, and management information. The snapshot preserves the service attributes and the DNR’s free-text ecological comments, then joins each stand to held soil, wetland, and circa-1800 land-cover layers.
The result is asymmetric by design. The service returned 424 exact stand intersections on Beaver Island and none on Garden, High, Hog, Whiskey, North Fox, or South Fox. A zero result means that this DNR service returned no stand polygons in that island frame; it does not mean those islands lack forests or that another public or tribal inventory does not exist.
Island query results
| Island | Survey context | Returned bbox features | Exact DNR stand intersections | Clipped stand area (km²) | Source stand acres |
|---|---|---|---|---|---|
| Beaver Island | MI029 / immediate Beaver group | 424 | 424 | 50.334 | 12,435.6 |
| Garden Island | MI029 / immediate Beaver group | 0 | 0 | 0 | 0 |
| High Island | MI029 / immediate Beaver group | 0 | 0 | 0 | 0 |
| Hog Island | MI029 / immediate Beaver group | 0 | 0 | 0 | 0 |
| Whiskey Island | MI029 / immediate Beaver group | 0 | 0 | 0 | 0 |
| North Fox Island | MI089 / Fox Islands | 0 | 0 | 0 | 0 |
| South Fox Island | MI089 / Fox Islands | 0 | 0 | 0 | 0 |
The Beaver stand footprint is about 50.334 km² within the 151.076 km² held OSM
island frame. That is inventory coverage, not a claim that the remaining area
is unforested, unmanaged, or privately owned. The source ACRES values sum to
12,435.6 acres and are retained separately from the equal-area clipped geometry
calculation.
Beaver Island cover-type structure
The largest current DNR cover-type groups by clipped area are:
| Cover-type group | Stands | Clipped area (km²) | Source codes represented |
|---|---|---|---|
| Northern Hardwood | 75 | 14.040 | 4110, 4111, 4112, 4115, 4116, 4117, 4119 |
| Lowland Coniferous Forest | 43 | 6.790 | 6120, 6121, 6122, 6128, 6129 |
| Lowland Deciduous Forest | 68 | 6.739 | 6111–6119 |
| Lowland Mixed Forest | 23 | 5.449 | 6131, 6132, 6139 |
| Mixed Upland Deciduous | 27 | 3.438 | 4190, 4191, 4193, 4199 |
| Aspen | 30 | 2.992 | 4130, 4133, 4135–4139 |
| Other Upland Conifers | 11 | 2.129 | 42350, 42360, 42380, 42390 |
| Lowland Shrub | 27 | 2.108 | 622, 6220, 6221, 6224, 6225, 6229 |
| Emergent Wetland | 47 | 1.854 | 623, 6230, 6233, 6239 |
| Natural Pines | 9 | 0.529 | 42200, 42201, 42210, 42260 |
One additional stand covers 0.613 km² but has no L4Covertype; the generated
index keeps it in an explicit “Unclassified / no L4 cover code” bucket so the
424-stand total remains complete.
The cover groups are DNR inventory classifications, not direct translations of the MNFI natural-community classes. For example, a “Northern Hardwood” stand may be part of a larger mesic forest occurrence, while a lowland-conifer stand may include rich or poor conifer swamp, wet meadow, or other transitional conditions. The raw fields and comments are preserved for that finer reading.
DNR ecological comments and MNFI connectivity
The DNR comments contain direct ecological classifications or descriptions in 188 of the 424 Beaver stand records. After normalizing capitalization and trailing score text, the most common classifications are:
| Normalized DNR comment classification | Stands |
|---|---|
| Mesic Northern Forest | 36 |
| Dry-mesic Northern Forest | 22 |
| Northern Wet Meadow | 20 |
| Northern Hardwood Swamp | 15 |
| Rich Conifer Swamp | 13 |
| Hardwood-conifer Swamp | 10 |
| Northern Shrub Thicket | 10 |
| Boreal Forest | 16 |
| Open Dunes | 3 |
| Bog, Poor Conifer Swamp, Emergent Marsh, Great Lakes Barrens, and Sand and Gravel Beach | 1 each |
These classifications are valuable because they show DNR stand-level comments
using the same broad ecological vocabulary as the MNFI report. They are not a
geometry-based EO join: the DNR layer’s MNFICommunity field is generally not
populated in this snapshot, and the text comments do not provide an MNFI EO
boundary or ID for every stand.
The comments also contain direct wildlife and tree-management signals. Across the 424 stands, the normalized comment index finds deer in 219, swamp in 175, wet in 155, ash in 152, conifer in 143, hardwood in 138, cedar in 118, birch in 100, aspen in 96, beaver in 80, fir in 71, wildlife in 58, pine in 42, oak in 15, invasive-species language in 12, spruce in 11, and grouse in 10. These are substring counts over DNR comments and management notes, not abundance estimates or new species observations.
One representative comment describes a mesic northern forest as good wildlife habitat with flushed grouse, scattered aspen, red oak, ash, birch, and red maple, plus wet pockets. Other comments connect old beaver flooding to tree mortality and regeneration of lowland hardwood and swamp-conifer species, and describe dune-ridge mosaics of upland oak-pine and lowland cedar-fir. The raw GeoJSON preserves those source comments for review.
Stand-level physical context
Each clipped stand carries spatial context from the held layers. The summary below aggregates only the areas inside DNR stand polygons on Beaver Island; it does not describe the whole island.
Current SSURGO context
| SSURGO map-unit symbol | Intersected area inside DNR stands (km²) |
|---|---|
| Rc Roscommon sand | 14.659 |
| KLB Kalkaska-Leelanau association | 7.995 |
| BdA Belding-Breckenridge sandy loams | 6.045 |
| Ak Alpena, Kiva, and East Lake soils | 4.210 |
| LU Lupton-Cathro association | 3.438 |
| TC Tawas-Carbondale association | 2.318 |
| An Angelica-Ensley loams | 2.133 |
| Gr Greenwood peat | 1.767 |
| DDB Deer Park-Dune land association | 1.748 |
This makes the USDA survey’s soil vocabulary useful at stand scale, while keeping current map-unit boundaries distinct from the MNFI narrative’s site descriptions.
NWI wetland context
The largest NWI category inside DNR stand polygons is Freshwater Forested/Shrub Wetland at 23.279 km², followed by Lake (0.550), Freshwater Emergent Wetland (0.283), Freshwater Pond (0.062), and Riverine (0.021). A stand can contain a mapped wetland portion without being wholly a wetland, and NWI is not a legal wetland delineation.
Circa-1800 vegetation context
The historical land-cover categories intersecting the DNR stand footprint are:
| Circa-1800 cover type | Intersected area inside DNR stands (km²) |
|---|---|
| Beech-sugar maple-hemlock forest | 33.900 |
| Mixed conifer swamp | 11.686 |
| Mixed hardwood swamp | 1.483 |
| Cedar swamp | 1.431 |
| Lake/river | 0.375 |
| Shrub swamp/emergent marsh | 0.300 |
| Black ash swamp | 0.205 |
| Sand dune | 0.079 |
This is a particularly useful historical-to-modern bridge: the same current public stand footprint can be read against DNR’s present cover type, SSURGO map-unit context, NWI wetland class, and the GLO-derived circa-1800 reconstruction. The comparison is spatial correspondence, not proof that a modern stand is continuous with a particular 1800 forest patch.
Evidence limits
The official service is a public forest inventory and its coverage is not the same thing as archipelago forest coverage. The query returned no stand polygons for six islands, so the archive must not interpret those zeros as ecological absence. The OSM boundaries used for clipping are research boundaries rather than cadastral or legal lines. Spatial intersections with SSURGO, NWI, and circa-1800 cover are calculated context, not causation, legal status, or an MNFI occurrence delineation. The snapshot is dated and should be refreshed if current stand conditions or DNR edits matter.
See also
- Forest types and tree history
- Wildlife and bird life
- Wetlands, inland waters, and hydrology
- Pre-settlement landscape and environmental history
- MNFI Natural Community Surveys of Beaver Island Archipelago, 2017
- MNFI soil, vegetation, tree, and wildlife crosswalk, 2017
- Soil survey of Charlevoix County, Michigan, 1974
Sources
- Official service metadata describes stands as relatively homogeneous polygons with cover type, age, canopy, stocking, origin, and management attributes. The service is a public forest inventory and is updated through the DNR inventory cycle; it is not a complete forest map of private land or all natural communities.research · forest_inventory · sources · mdnr_mifi_stand_covertype_layer_2026-08-02
- Raw project snapshot of the DNR stand-covertype bounding-box queries for the seven named island frames.Preserves the returned service geometries and attributes, with query-island and bounding-box audit fields. Exact island clipping is performed separately. No public copy of this file is known; the archive holds one and can provide it on request.research · forest_inventory · sources · mdnr_mifi_stand_covertype_query_2026-08-02
- Project-generated DNR forest-inventory stand crosswalk index.Summarizes exact island intersections, stand areas, cover-type groups, DNR comment classifications, and intersections with held SSURGO, NWI, and circa-1800 land-cover layers. No public copy of this file is known; the archive holds one and can provide it on request.research · forest_inventory · indices · mdnr_forest_inventory_island_stands_2026-08-02
- Project-generated clipped DNR forest-inventory stand layer.Retains source stand attributes and clipped geometries in WGS84, with equal-area-derived areas and per-stand soil, wetland, and circa-1800 context arrays. No public copy of this file is known; the archive holds one and can provide it on request.research · forest_inventory · indices · mdnr_forest_inventory_island_stands_2026-08-02
- Provenance sidecar for the DNR forest-inventory snapshot and crosswalk.Records service metadata, query frames, source checksums, output checksums, area CRS, and the local intersection method. No public copy of this file is known; the archive holds one and can provide it on request.research · forest_inventory · indices · mdnr_forest_inventory_island_stands_2026-08-02.provenance
- Described in this archive: MNFI Natural Community Surveys of Beaver Island Archipelago, 2017.The crosswalk uses the MNFI index only for island-level occurrence counts and preserves DNR comment classifications as a separate source; it does not claim DNR stand/MNFI EO overlap.research · island_farming · indices · mnfi_natural_community_surveys_beaver_archipelago_2017_11
- The exact input paths and checksums for all contextual layers are recorded in the provenance sidecar.soils · ssurgo_mapunit_polygons
Added 3 August 2026. Recent changes
Cite this article
Beaver Island Archive, “Michigan DNR public forest inventory stand cover types, 2026 snapshot”, https://beaverislandarchive.org/documents/mdnr-forest-inventory-stand-covertype-2026/, accessed [date], citing Michigan Department of Natural Resources, Michigan Forest Inventory System, Public Forest Inventory Data, Stand Covertype layer (layer 3), retrieved 2 August 2026. (and 6 further sources listed on the page).
Last revised 2026-08-03. Fill in [date] with the date you read it — this page is static and cannot know that.
BibTeX for “Michigan DNR public forest inventory stand cover types, 2026 snapshot”RIS for “Michigan DNR public forest inventory stand cover types, 2026 snapshot”