New Study Finds Forests Conservation Measures Successful in Reducing Maryland Forest Loss, State Has Opportunity to Achieve Net Forest Gain

November 16th, 2022

30 Years After Forest Conservation Act, New Monitoring Data Assess the Health of One of Maryland’s Most Important Natural Resources

Queenstown, Md. – A new study commissioned by the Harry R. Hughes Center for Agro-Ecology and conducted together with the Chesapeake Conservancy and the University of Vermont is the most comprehensive study of Maryland’s forest cover and tree canopy ever completed.

The study finds that over time, Maryland’s rate of forest loss has declined and the state is approaching a goal of achieving no net forest loss. With State priorities focused on tree plantings and increased funding available for land protection and agricultural conservation practices, the state has the opportunity to soon achieve no net forest loss and tip the balance towards forest gain.

At regional and county scales, patterns of forest change vary widely, and some concerning trends continue. Counties in central Maryland with rapid development and population growth experienced greater rates of loss, especially loss associated with development. While forest levels as a whole are stabilizing, continued urbanization is fragmenting forests and encouraging spread of invasive species. Fragmentation and invasive species spread are likely to continue given current patterns of change, especially in rapidly growing areas of the state.

The Technical Study on Changes in Forest Cover and Tree Canopy in Maryland, or Maryland Forest Technical Study, uses high-resolution data to analyze forest and tree canopy change at the local scale and provide a greater understanding of the key drivers of change. Insights derived from the study may be helpful to develop recommendations and policies that shift the balance to meet Maryland’s forest cover and tree canopy goals. The partners made several recommendations as a result of this study, including improving monitoring through technological innovation, addressing the loss of tree canopy outside forests and assessing causes of tree canopy change within forest blocks.

The study was conducted by the Hughes Center, Chesapeake Conservancy and the University of Vermont Spatial Analysis Lab in consultation with the Chesapeake Bay Program, and an Advisory Committee comprised of the Maryland Department of Natural Resources, the Department of the Environment, the Department of Planning, the Department of Agriculture and the Chesapeake Bay Program. In an effort to improve Maryland’s statewide inventory of forest and tree canopy cover and assess forest and tree canopy change and the effectiveness of Maryland’s forest and tree programs, the Maryland Senate enacted a bill authorizing the study in 2019.

This report was supported by a grant from the Harry R. Hughes Center for Agro-Ecology utilizing funding from the State of Maryland, awarded following an open Request for Proposal (RFP) process.

As the Forest Conservation Act reached 30 years in practice in 2021, this is an important occasion to mark the successes of Maryland’s forest protection legislation and reflect on opportunities to further leverage forests and tree canopy to enhance benefits for habitat, water quality protection, climate resilience and mitigation, human health and environmental justice.

To review the methodology and read the study, “Technical Study on Changes in Forest Cover and Tree Canopy in Maryland,” in its entirety, visit flji.0478yigou.com/mdforeststudy2022.

Additionally, an associated online StoryMap provides the opportunity to view and interact with data and results produced in support of this study: cicgis.org/portal/apps/storymaps/stories/b519e88ccc8c4c4c8d4c870f64e210ed.

Quotes

“The findings from this study are key for decision-makers at both the statewide and local levels as they consider future strategies for trees and forests,” said Harry R. Hughes Center for Agro-Ecology Executive Director Dr. Kate Everts. “This study comes at a critical time in Maryland as populations continue to increase and as we consider the future of Chesapeake Bay restoration. The Hughes Center is grateful for the opportunity to release this study and help tell the story of changes among our forests and trees so that science-based decisions can drive Maryland’s approach to protect them into the future.”

“It is notable that since 2000, forest loss slowed across Maryland while population grew nearly 17% and areas of loss are concentrated in a few rapidly growing counties,” said Chesapeake Conservancy’s Vice President for Climate Strategy Susan Minnemeyer. “This study provides key insights into tangible progress in increasing tree cover and tools local governments can use for planning future forest investments. Forests are green infrastructure for strengthening our communities, providing clean water and greater climate resilience. ”

“Information is power,” said Chesapeake Conservancy’s Executive Vice President Mark Conway. “As our state works to restore the health of the Chesapeake Bay and deals with the effects of climate change, utilizing the latest high-resolution land cover data to study forest and tree canopy is one of the most valuable tools in our toolbox. Trees are our best protectors from storm surges, floods, sea-level rise and extreme temperatures. They play a major role in water filtration, stormwater mitigation, air pollution removal, climate resilience and carbon sequestration. Trees are one of Maryland’s most important natural resources. In fact, our health, our environment and our economy all depend on trees.”

“It is crucial that our elected officials have the best information possible to make informed decisions about our natural resources that impact the health of our residents and the viability of the landscapes that sustain us,” said University of Vermont Director of the Spatial Analysis Laboratory Jarlath O’Neil-Dunne. “We are proud to have assisted in this important project that sets the standard for statewide forest assessment.”

Key Findings

Maryland’s Existing Forest Cover and Tree Canopy

Maryland’s forests cover 2.448 to 2.566 million acres of the state’s land area, according to the USDA Forest Service Forest Inventory and Analysis (FIA) program and the Chesapeake Bay Program Office (CBPO). When tree canopy outside forests is included, the state’s total tree canopy covers an estimated 3.095 million acres (CBPO). Percent forest cover estimates range from 39-42% of the state’s total land area, depending on the dataset and approach used (FIA, CBPO). Findings from three independent data sources (FIA, CBPO, and the National Land Cover Dataset or NLCD) agree on similar trends in Maryland’s forests. Forest area has shown a slightly decreasing trend over 5- and 20-year intervals but with a trend toward stabilization in the past 10 years (-0.14% annually from 2013-2018; -0.23% annually from 1999-2019). The decrease in forest cover has been offset somewhat by an increase in tree canopy outside forests, resulting in a more modest decrease in the total tree canopy (-0.077% annually). Despite the slightly decreasing, yet now stabilizing, trend, the state’s tree canopy has been remarkably stable given considerable increases in human population over the same period (876,000 people or nearly 17% growth from 2000-2020).

(Note: See Table ES-1 on Page 9 of the study)

Potential Locations for Afforestation and Reforestation

This study identified 373,506 acres of potential afforestation and reforestation locations in Maryland. Prioritization of planting sites will rely on further evaluation of available locations providing the greatest benefits from increasing tree canopy, financial resources and landowner interest. If Maryland wants to increase its forest cover, afforestation and reforestation, along with protection for existing forest, will be essential.

Health and Quality of Maryland’s Forests

This study examined both fragmentation and disturbance (including from invasive species) in Maryland’s forests. Forest structure throughout the state can generally be described as a patchy mosaic interspersed with other land cover types and infrastructure. The analysis shows the forest landscape became increasingly fragmented from 2013 to 2018, with the majority of trees in forested areas classified as edge or small patches. These types of fragmentation often have less habitat value and higher vulnerability compared to interior or core forest and increase pressure on species that require large, continuous intact forest tracts. Ground observations at USDA Forest Service’s Forest Inventory and Analysis plots between 2013-2019 indicated that approximately 12% of forests in Maryland experienced recent disturbance, with invasive species being the largest risk factor. The most frequent invasive plant species were multiflora rose, Japanese honeysuckle, Nepalese Browntop, and garlic mustard. Over the last 20 years, many of Maryland’s ash and hemlock trees have suffered damage or death from the Emerald Ash Borer and Hemlock Woolly Adelgid infestations.

Chesapeake Bay Watershed Agreement of 2014: Progress towards Expanding Urban Tree Canopy Acres and Riparian Forest Buffers

The Chesapeake Bay Watershed Agreement of 2014 (2014 CBA) committed Chesapeake Bay jurisdictions to collectively plant a total of 2,400 acres of trees in urban areas (here meaning census urbanized areas and urban clusters) by 2025. This analysis identified 4,665 acres of new tree canopy cover in urban areas between 2013 and 2018, but a loss of 17,829 acres, for a net decrease of 13,164 acres). From 2018-2020 (following this study interval), at least 30,000 trees have been planted in urban areas, cumulatively amounting to 85 additional acres. However, this study still indicates a significant net loss of urban tree acreage over the years 2013-2020.

Maryland has also committed to planting trees in streamside areas until 70% of riparian areas in the Chesapeake Bay watershed are forested. Our desktop analysis found 33% of Maryland’s jurisdictions (8) have reached the 2014 CBA goal of 70% of riparian areas under forest, while four jurisdictions (Baltimore City, Dorchester, Somerset, and Wicomico) still have less than 50% tree canopy cover in riparian areas. Trees planted more recently were not detected, as it can take up to 10 years for new trees to appear in remotely sensed high-resolution imagery, though they still provide a significant addition to emerging canopy cover in the state.

Forest and Tree Canopy Changes

We note that patterns and drivers of tree canopy change (including tree canopy within and outside of forests) vary regionally. All but one region lost forest cover, and the region that gained was the Lower Eastern Shore region where the timber industry is active, signaling regrowth after extraction. All regions but Central Maryland experienced a net gain in tree canopy outside forests, indicative of forest fragmentation and tree planting. Central Maryland, representing the rapidly urbanizing Washington, D.C. suburbs, was the only region that experienced a loss of tree canopy cover from outside and within forest (Figure ES-2, p. 12). The distribution of tree canopy loss is highly skewed — two counties, Montgomery and Prince George’s, accounted for more than 44% of the state’s total tree canopy loss to development and six counties accounted for just under 70% of its tree canopy loss (see Figure 22 and Table 14 in the full report). These counties are Prince George’s, Montgomery, Anne Arundel, Charles, Calvert and Baltimore (Table 14 and Figure 22). Though there was a statewide trend toward forest fragmentation and development (Figure ES-3, p. 12), we also observed transitions of developed land to tree canopy, indicating an effort toward urban greening. The transition of forests to wetlands in coastal counties may be indicative of sea level rise. A parallel analysis found that Priority Funding Areas for development were more vulnerable to tree canopy loss, further indicating development as an important driver of change in the state.

Protected Areas Slow Forest Loss and Are Also a Source of Tree Canopy Gain

In 2018, 33% of Maryland’s forests and 9% of tree canopy outside forests were located within protected areas. Protected lands experienced a significantly lower rate of forest loss and a much higher rate of tree canopy increase compared with statewide rates. Protected areas had a net gain of over 2,200 acres of total tree canopy, demonstrating that protected areas offer a source of tree canopy gain in addition to protecting forests from loss.

Forest Mitigation Banking

Across the state, 81.1% of reported mitigation bank acres protect existing forest, with newly planted forest only making up 18.9% of forest bank acres. This suggests that steps may need to be taken to encourage the creation of planted forest banks, since forest banks can no longer be created from existing forest (at least until June 30, 2024 per the provisions of the Tree Solutions Now Act of 2021). The evidence does not suggest a meaningful relationship between fee-in-lieu rates and the market for mitigation banks. However, higher fee-in-lieu rates could stimulate the creation of newly planted forested mitigation banks in the future. The market for forest mitigation banking varies considerably between counties.

Tree Planting Programs throughout Maryland

In 2018 and 2019, government and private tree planting programs were responsible for the planting of an estimated 1,853 cumulative acres, more than half of which was in response to the Forest Conservation Act (Task 7). This trend toward increasing tree planting should continue and accelerate with implementation of the Tree Solutions Now Act of 2021 that sets the goal of planting an additional 5 million trees (~12,500 acres) over the eight-year period from 2023 to 2031. There is ample land area providing opportunity for planting trees; this study identified over 373,500 acres of potential afforestation and reforestation sites in Maryland on non-agricultural lands. Planting only 3.3% of the identified area would enable Maryland to reach its Tree Solutions Now Act goal.

Selected Summary Statistics

General and Regional Information:

3,095,000 acres of forest and tree canopy outside of forest exist within Maryland for 2018 (or 48% of the state’s total land area).
Allegany County has the most percent tree canopy cover (forest and tree canopy outside of forest), while Baltimore City has the least.
373,506 acres of potential afforestation and reforestation exist throughout the state.
All core forest sizes (large, medium, small) decreased in mean and median area between 2013-2018, except for a slight median increase in large cores.
Census urbanized areas experienced a net decrease of 13,164 acres of tree canopy, with the largest losses around the Washington, D.C. and Baltimore suburbs.
Eight jurisdictions have reached the 2014 Chesapeake Bay Agreement goal of 70% forested riparian areas; four jurisdictions have under 50% tree canopy cover in riparian areas.
Timber harvests on both private and state lands from 2013 to 2021 total 149,156 acres; Garrett County had the highest total harvest, consistent with its large forested acreage.
Priority funding areas (PFA) experienced a greater loss of forest and tree canopy outside of forest within them (9,583 decrease) compared to non-PFA areas.
There is a lower rate of forest loss in priority protection areas compared to the state average (0.44% vs 0.70%, respectively), indicating while protected and sensitive lands still experience loss, that regulations to protect the land are working to preserve forest.

Fragmentation, Disturbances, Diseases and Insects:

Patches of forest increased by 3,252 acres from 2013-2018.
Forest edges are the predominant fragmentation type (by acreage).
Suppressive vegetation has the most detrimental impact on forests in terms of disturbances.
Invasive plant species, multiflora rose most commonly, were found across two-thirds of the USDA Forest Service’s Forest Inventory and Analysis (FIA) plots across the state.
The invasive Emerald Ash borer has impacted an estimated 83% of ash volume in the state; forests and trees across the state are otherwise also at risk from Hemlock Woolly Adelgid and Beech Bark Disease.
Western watersheds of the state are most at risk of insect and disease, with more than 25% of treed areas at risk in some regions, and moderate risk across central Maryland and the Eastern Shore.

Programs:

33.2% of forests in the state are in existing protected lands; there was only a slight decrease (0.03%) in forest within existing protected lands from 2013-2018, again indicating protecting land is conducive to preserving forest.
18 of the 22 counties governed by the Forest Conservation Act (FCA) have provisions for forest mitigation banking programs, and mitigation banks have been created in 15 of those counties.
The market for banking varies greatly between counties, with the percentage of development projecting within a county that rely on banking credits for mitigation range from 0 to 80%.
Across the state as a whole, forest mitigation banks are dominated by previously existing forest, which comprises 13,997 acres or 81.1% of reported forest bank area, with newly planted forest banks only making up 3,261 acres or 18.9% of bank area.
Maryland has a number of private and government tree planting programs that vary greatly in purpose and scale. In 2018 and 2019, approximately 550,533 trees and an additional 477 acres were planted through these programs.

###