Previous Page:
4.5 Status of Non-native Vascular Plants

Scroll for more

Getting Started

Navigating this Report

 

This report consists of two companion reports—one for the Northern Operating Area and one for the Southern Operating Area. All the features necessary to navigate within each report as well as switch between reports are included in the bookmark on the left of the screen. These features include:


Main Menu

The main menu is accessed through the hamburger menu in the "bookmark" on the left-hand side of the page. This report is divided into five chapters. From this menu, you can access each of the main chapters and their sections from anywhere in the report.

Tip: The down arrowhead expands when you are viewing a chapter within the hamburger menu. You can quickly navigate to any section within a chapter by making a selection from the expanded menu.

North and South Reports

Click these icons to navigate between the reports for the Northern Operating Area and Southern Operating Area. 

 

Information Guide

Click on the "information" icon in the left menu to access the report navigation guide. You can access this at any time without leaving the page you’re on.

The "page turner" arrows at the bottom left of your screen will sequentially take you through the report, page by page. For example, press the right arrow to move from Section 2.1 to Section 2.2.

Tip: If you’re interested in the full report, we encourage you to start with the Introduction found in Chapter 1, and use the page turner function (arrows on the bottom left of the page) to sequentially navigate through the report.

Tolko’s Northern Operating Area spans 42,771 km2 in northwestern Alberta, where coniferous trees are harvested. Responsible forest management requires a clear understanding of how forestry operations affect land cover and biodiversity, and monitoring can help identify areas for improvement.

Status of Land Cover

Summary of Land Cover Results

Highlights of land cover results include:

  • As of 2021, the total human footprint was 10.0% in the Northern Operating Areas. Forestry (7.3%) was the largest human footprint but this is reduced to to 5.3% when accounting for the regeneration of harvested stands. Energy (2.1%) was the next most common footprint type.
  • Total human footprint increased by 5.8 percentage points between 2000 and 2021; these increases were driven by the creation of forestry footprint. The vegetation types most impacted by human footprint were White Spruce and deciduous stands during this time period.
  • While human footprint is an important contributor to land base change, fire added 8–11% of disturbance in upland stands between 2010 and 2021, in some cases disturbing more area than forestry footprint.
  • Wildfires in 2023 burned 13.6% of the Northern Operating Area, with burn rates 6–14 times the combined human footprint and fire rate from 2010–2021. Burn rates were high across all vegetation types, lowering the average age from 83 years in 2021 to 71 years in 2023.
  • Undisturbed native habitat covered 90% of the Northern Operating Area in 2021, a drop of 3.3. percentage points from 2010. Interior native habitat was 73.5%, 46.0%, and 11.2% at 50 m, 200 m and 500 m away from human footprint respectively. 
  • Linear footprint density (circa 2021) was estimated to be 3.3 km/km2 in the Northern Operating Area; conventional seismic lines at 2.9 km/km2 were the predominant linear feature.

In the Northern Operating Area...

...forestry footprint covers 7.3%...

...undisturbed native vegetation covers 90% and...

...wildfires in 2023 burned 13% of the region.

Status of Biodiversity

Summary of Biodiversity Results

Highlights of biodiversity results include:

  • The cumulative effects of land disturbance on 586 common species in the Northern Operating Area resulted in an average habitat suitability of 95%, as measured by the Biodiversity Intactness Index. 
  • Average intactness by species group ranged from 94% for birds and vascular plants to 97% for mites, with some individual species within each group showing lower intactness. Deviations from intactness were due to changes in habitat suitability, either decreases or increases, as a result of human footprint compared to reference conditions.
  • Habitat suitability was lower within human footprint compared to the native vegetation it replaced for ~59% of species across six taxonomic groups. Lichens and mosses were the most negatively affected by human footprint, while other species groups, particularly birds and vascular plants, exhibited a broader range of responses to different sectors.
  • Forestry resulted in stronger negative effects on species reliant on old, upland forest stands while all sectors increase habitat suitability for species associated with open and/or disturbed habitat.
  • The net effect of natural changes on the land base, including fire and aging of naturally disturbed stands, was greater than the net effect of human footprint, ranging from -21.6% to +29.3% change in habitat suitability for individual species.

Highlights for species of management interest include:

Moose. ABMI

Moose density was 0.27 individuals/km2 in the Northern Operating Area. Much of the region provides moderately suitable habitat for Moose, with lower suitability in the north. 

Woodland Caribou.

In Woodland Caribou range, tracking vegetation regrowth using remote sensing tools is an area of active research. 

Arctic Grayling. S Shankar

Arctic Grayling population status is rated as having low to moderate population densities in more than 50% of the Northern Operating Area.

Cape May Warbler. Paul Reeves

There are 58 species of conservation concern in the Northern Operating Area including 14 federally and/or provincially listed species.

Smooth Brome (Bromus inermis).

Nine non-native vascular plant species were detected across the sampled sites with non-native vascular plants present at 30% of the locations.

Next Steps

Responsible forest management requires a clear understanding of how forestry operations impact land cover and biodiversity. Monitoring can help identify opportunities for improvement.

Results from this report set the stage for openly addressing key questions such as:

  1. What components of biodiversity are the most sensitive to forestry activities, and what might be done to minimize impacts?
  2. What are the cumulative effects of resource development on biodiversity and how effective are efforts to manage regional cumulative effects?  
  3. What is the impact of forestry on biodiversity as compared to other land uses, such as energy?

Overall, the land cover and biodiversity results presented in this report establish current conditions, and in some instances trend, that can be used to evaluate forest management objectives.

With Tolko's Northern Operating Area at least 95% intact today, there is significant opportunity for land managers to make informed and deliberate choices to maintain or increase biodiversity intactness over time. As development continues to unfold in the region, the ABMI will continue to measure and report on the changing state of land cover and biodiversity.

We are grateful for the support of the ABMI's delivery partners.