Adirondack Wilderness

Adirondack Wetlands: Heron Marsh from the Floating Bridge at the Paul Smiths VIC (7 September 2013)
Adirondack Wetlands: Many of the plant and animal species that depend on wetlands for their habitats could be left with nowhere to live as a result of climate change and other stressors like pollution and urban development. Heron Marsh at the Paul Smiths VIC (7 September 2013)

After the glaciers that sculpted the Adirondacks retreated some 13,000 years ago, glacial ice was replaced by tundra, then by boreal forests. These boreal forests were later replaced by a mix of boreal and temperate forests that comprised the Adirondack wilderness of the early 17th century, when European settlers arrived in the New World. A harsh climate and poor soil had discouraged the Native Americans who occupied the valleys around the mountains from permanent residence in the mountains and initially inhibited exploitation by the European newcomers.

In time, however, the Adirondack wilderness that greeted European settlers succumbed to economic pressures that were reshaping the landscape throughout North America. The wilderness we see today is not the original, post-glacial wilderness, but a recovering wilderness. Natural forces are gradually repairing the initial man-made scars of logging, mining, and farming; however, this process is shaped by ongoing human impacts, including development, acid rain, and climate change.

The Post-Glacial Adirondack Wilderness

Trees of the Adirondacks:  Eastern White Pine in the Elders Grove.  Photo by Sandra Hildreth.  Used by permission.
Adirondack First Growth Forest: This tree, one of about fifty Eastern White Pines in a twelve-acre site near Paul Smiths, is part of an Elders Grove which may have germinated in the wake of a windstorm or other disturbance that struck the region between 1675 and 1680. Although the trees surrounding the site have been logged, the elders were spared, possibly because early loggers were unsure of property lines.

The retreat of the ice sheet in response to a warming climate prompted a northward migration of plant species, returning from warmer southern regions. The record of their return (and, in some cases, subsequent departure northward) is written in fossilized sediments preserved in the bottom of bogs or in the bottom sediments of small lakes.

  • The post-glacial colonization process began with a handful of tundra-dwelling species, such as Dwarf Birch, Alpine Club Moss, and Northern Blueberry. Most disappeared, but a few still persist on the Adirondack High Peaks.
  • Then, as the climate gradually warmed, boreal forests of spruce and fir appeared and gradually replaced the arctic tundra. These early post-glacial forests were initially dominated by White Spruce, which later gave way to Balsam Fir and, in some places, Paper Birch (the first hardwood to arrive, about 10,000 years ago). Eastern White Pine appeared around 9,000 years ago.
  • By the time the warming period peaked (about 6,000 years ago), many hardwood species had reappeared in the Adirondacks, including Yellow Birch, Sugar Maple, and American Beech.
  • As the region started to cool again, Yellow Birch increased; and Red Spruce appeared, quickly becoming the dominant conifer.
  • By the beginning of the 19th century, the virgin forests that greeted the first land surveyors and settlers reflected about a 50/50 balance of softwoods (conifers) and hardwoods (deciduous trees).

Little of this early wilderness remains. How much of the Adirondacks is first-growth forest (forest that has not been disturbed by logging, mining, farming, or other human impacts)? The short answer is that we don't know, because these areas have yet to be mapped. Nor is there general agreement on what constitutes "first growth" (areas untouched by human impacts) and "old growth" (areas that were minimally disturbed and left undisturbed for a century or more). As a result, estimates vary.

  • Botanist Edwin Ketchledge estimated that about 200,000 acres of forest (about 3% of the Adirondacks) could be considered first-growth.
  • Environmentalist Barbara McMartin estimated in 1994 that about 500,000 acres (8-9%) could be considered old growth, which she seems to equate with "relatively untouched forest," meaning that it was never logged or logged "minimally."
  • In 2002, Bruce Kershner estimated that old-growth forest in the Adirondacks consisted of about 150,000 acres.
  • Jerry Jenkins estimates that about 586,000 acres (9.6% of the Park) has never been logged or seriously affected by storms or fire.
  • Botanist and forest historian Michael Kudish estimates that perhaps 5-10% of the Adirondacks is first-growth forest, most of it in locations not accessible to – or profitable for – loggers.

In any event, the vast majority of the pre-settlement forests have disappeared, having experienced at least one major impact from human activity.

Wilderness Invaded: Farming the Adirondacks

Farming in the Adirondacks: Farm Field along the Harrietstown Road in Franklin County.
Farming in the Adirondacks: Most remaining farms within the Adirondack Park are on the periphery, in the Champlain and St. Lawrence valleys. Very few farms remain in the Adirondack interior. Farm field on Harrietstown Road in Franklin County.

The impact of agricultural land-use in the Adirondacks was and continues to be limited by the fact that most places within what is now the Adirondack Park make lousy farmland. Soils are thin and infertile; winters are long; and the growing season is short. Native Americans settled in the lowland areas on the (mainly southeastern) periphery of the Park, but (according to most accounts) wisely avoided permanent settlement in the mountainous areas, using them only in the summer to hunt and fish.

Starting in the late 17th century, the extent of agricultural land use in the Adirondacks increased significantly, as Europeans invaded the lowlands where the soil is more fertile and the slopes less steep.

  • By 1800, only thin strips of land on the southern edge of what is now the Adirondack Park had been cleared for farming.
  • By 1885, according to a map produced by the Sargent Commission, 27.8% of the Adirondack Park had been cleared, some for fuel for forges and bark for tanneries and some (the valleys) for agricultural use.
  • The Adirondack upland in the interior was settled last, in the mid-19th century, and, in most areas, never cleared for agriculture, because the land was so unsuitable. Some lowland areas near the major rivers were settled by farmers; other farms appeared near the Great Camps to provide agricultural products for the wealthy who summered there.

Many of these farms had been abandoned by the early 20th century, as Adirondack farms on more marginal ground succumbed to competition from farms in more fertile areas outside the park. With the exception of a few farms in small pockets of arable land in the Adirondack interior, farming is now limited to the Champlain and St. Lawrence Valley areas.

  • Some old farm fields were left to fill in naturally through a process called old field succession.
  • Other areas were planted with conifers, such as Red Pine and Scotch Pine, as part of a reforestation program sponsored in the 1920s and 30s by the state.

In any event, the abandonment of Adirondack farmland has resulted in an expansion of second-generation forest and, ironically, a loss of some of the stunning vistas of the early and mid-twentieth century, when the open fields framed breathtaking views of the mountains beyond.

Wilderness Ravaged: Exploiting the Forests

Trees of the Adirondacks: Red Spruce at the Paul Smiths VIC (28 July 2012)
Logging in the Adirondacks: Red Spruce trees were a target of commercial logging operations, starting in the 1830s, in part due to the fact that it floats, allowing loggers to transport the logs by water to mills on the Adirondack periphery. Red Spruce at the Paul Smiths VIC (28 July 2012).

The logging industry changed huge swathes of the Adirondack landscape and represents the dominant human impact in the 19th and early 20th centuries. The first species to be targeted by loggers was Eastern White Pine, prized because its height and straight grain made it useful for constructing the masts of sailing ships. The most accessible stands of Eastern White Pine were in the southeastern region and along Lake Champlain, near established waterways. These were largely gone by 1830, although the ecological damage was limited to those areas where large stands of pine had flourished.

More important ecologically was the harvest of Eastern Hemlock. Hemlock bark, rich in tannin, was stripped and used to turn cow hides into shoe leather. The exploitation of hemlock emerged as an important part of the regional economy, beginning in about the middle of the 19th century. By the 1890s, when more profitable opportunities appeared in southern New York and Pennsylvania, more than a million acres of Adirondack forest land, much of it in the Lake Champlain and Lake George basins, had been cleared to obtain hemlock.

Logging the Adirondacks: Spruce Logs above the dam on the Boreas River.  New York State Archives.
Logging the Adirondacks: Spruce logs float, allowing loggers to exploit spruce forests and float the logs down rivers to sawmills on the edge of the mountains. Spruce logs above a dam on the Boreas River. New York State Archives.

It was the quest for Red Spruce that led loggers deeper into the Adirondack interior. Red Spruce, although generally smaller than Eastern White Pine, has a straight grain and is easily cut and planed. It was also more abundant than Eastern White Pine, representing perhaps a quarter of the Adirondack forest at the time. The first wave of logging began in the 1830s and peaked in 1890, during which time loggers exploited spruce flats on river drainages. The heaviest exploitation during this time was in the eastern part of the Adirondacks, where the spruce logs were floated down rivers to feed saw mills in Glens Falls. The development of logging railroads allowed spruce logging operations to move into the less accessible regions.

The logging railroads also allowed loggers to turn their attention to hardwoods, which had previously escaped destruction in the Adirondack interior because hardwoods do not float and so cannot be transported via rivers. By the turn of the century, the railway network was being expanded and mills were being built to exploit the hardwoods. By 1914, loggers were removing forests at a rate five times the rate of growth.

In the wake of logging operations and the railroads came fire. Loggers during this period left the tops of trees on the ground, providing fuel for fires, some of which were started by sparks from wood-burning engines. The damage done by the fires was intensified because this period of railway expansion and intense cutting in the late 19th and early 20th centuries coincided with several years of serious drought. According to estimates derived from a 1914 state Conservation Commission report, an estimated 850,000 acres or 14% of the land within the current boundaries of the Adirondack Park burned during this period.

These fires have had a longterm impact on forest dynamics in the Adirondacks. For instance, the most common birch in pre-settlement Adirondack forests was probably the Yellow Birch.  Widespread post-logging fires in the early 1900s disproportionately benefited the Paper Birch, but now many of these relatively short-lived trees are approaching the end of their life cycle and dying out, to be replaced by other species.    

Wilderness Ravaged: Exploiting the Minerals

Mining in the Adirondacks: Iron Plant in Mineville. New York State Archives.
Mining in the Adirondacks: Iron Plant in Mineville. New York State Archives.

Exploiting the Adirondacks' mineral resources had a somewhat less pervasive impact on the environment than those industries involved in exploiting the forests. Mining began in the mid-1700s. Adirondack mines produced iron, titanium, wollastonite, and garnet. The iron and titanium mines have closed; mines extracting nonmetallic minerals and the zinc ores continue to be worked.

The most enduring and widespread impact of mining in the Adirondacks is associated with the use of hardwood to make charcoal for iron production. In the late 19th century, an estimated quarter of a million acres were clear-cut to make charcoal for the iron industry. Much of the cutting was concentrated near roads and railways, helping to create an image of a ravaged landscape that contributed to public pressure to save the Adirondacks.

The Recovering Wilderness: Ongoing Threats to Wilderness

Thanks in part to changes that undermined the economic viability of these activities and in part to the formation of the Adirondack Park to curtail and reverse the damages associated with farming, logging, and mining, the vast majority of woodland in the Adirondacks is in some stage of recovery from the initial human impacts summarized above, if, by "recovery", we mean: "Have forests returned to areas denuded by agriculture or logging?" The logged-over woodland and fields have been largely reclaimed by vegetation. 

Complicating this ongoing process is the fact that habitats in the Adirondacks are simultaneously coping with a cocktail of ongoing assaults, most notably in the form of air pollution (acid rain and mercury contamination), tourism, residential development, and a warming climate as well as natural disturbances such as blow downs and larger-scale natural events like the ice storm of 1998 and the hurricane of 1950.

Trees of the Adirondacks: Sugar Maple on the Heaven Hil Farm trails in Lake Placid
Acid Rain: Sugar Maple, one of the most economically and ecologically important trees in the Adirondacks, has been heavily impacted by acid rain, probably in combination with warming temperatures. A 2015 analysis of growth rings from hundreds of trees across the Adirondack Mountains revealed a decline in the growth rate for a majority of sugar maple trees after 1970. Sugar Maple on the Heaven Hill Farm trail.

Air Pollution: Acid Rain and Mercury Deposition:  Acid deposition and mercury deposition are two components of air pollution affecting Adirondack ecosystems.  Both are consequences of fossil-fuel combustion;  both have caused significant environmental harm to the Adirondacks. The Adirondack region is among the most acid-impacted regions in North America.  More than 80 percent of the acid rain that falls on the Adirondack Park is generated outside of New York State, mainly by coal-fired power plants and fossil-fueled automobiles.

  • The most dramatic impact of acid deposition on the Adirondack ecosystem is on the lakes, streams, wetlands, and other aquatic environments.  Research conduced by the Adirondack Lakes Survey Corporation (ALSC) from 1984-1987 indicated that nearly 25% of the waters had pH values of 5.0 or less and that forty eight percent of the waters had little or no buffering capacity.  In 1985, more than 700 Adirondack lakes and ponds were found to be too acidic to support their native life. In 1998, more than 500 lakes and ponds out of 2,800 in the Adirondack Park were too acidic to support the plants and fish that once existed there.
  • Acid deposition has stressed Adirondack forests as a whole (primarily by reducing calcium levels in the soil and increasing the trees' vulnerability to weather and insect damage), shifting the composition of the forest in ways which will affect the ecosystem for decades (if not centuries) to come.  Two species have experienced particularly heavy losses: Red Spruce and Sugar Maple. In regard to the Red Spruce, acid rain leaches calcium out of the needles and reduces the needles' ability to tolerate freezing temperatures. Acid rain also interferes with the tree's ability to acquire nutrients from the thin Adirondack soils. This combination of reduced freeze tolerance and nutrient stress, which makes the trees more susceptible to insects and disease, is thought to be responsible for the loss of roughly half of the high-altitude spruce forests in the Adirondacks. Researchers have also linked acid rain to the decline of Sugar Maples, which appear to be highly vulnerable to the loss of calcium in the soil caused by the nitric and sulphuric acid in acid rain. 
  • The direct effects of acid rain reverberate up the food chain, with negative consequences for Adirondack wildlife.  Acidic water in Adirondack lakes disrupts the reproductive system of freshwater macro-invertebrates, plants, and fish populations.  Water-dependent amphibians such as frogs and salamanders are also affected.  Aluminum leaches from the soil into the water, altering the chemistry and clogging the fish's gills. Hundreds of lakes and ponds once teeming with trout and tadpoles, frogs and salamanders, are now clear and empty of such life. Although birds and mammals are not directly affected by water acidification, they are indirectly affected by changes in the quantity and quality of their food resources. Acid rain worsens mercury contamination of the park’s food web, by breaking down chemical compounds, turning harmless inorganic mercury) into the toxic organic form. Birds and mammals that rely on fish are particularly susceptible. Loons, for instance, are especially susceptible to mercury contamination because they eat fish and accumulate mercury in their bodies over their lifetime, causing behavioral changes that can effects that can lead to decreased reproductive success and, thus, to declining populations. Northern River Otters are also subject to mercury accumulation because of the high proportion of fish in their diet.  

The 1990 Clean Air Act, which restricted the fossil-fuel burning chemical emissions that increase acidity in the environment, has slowed the rate of damage and led to some recovery from these impacts.  Adirondack lakes have become somewhat healthier, which in turn is helping to protect fish from climate change. Some lakes that were once considered dead are now producing healthy brook trout again. However, some species, including the economically valuable Sugar Maple, have failed to recover and, in fact, have continued to decline further. As a result, in the western Adirondacks, where the lakes are most acidified and the soils poorest in calcium, maples have stopped reproducing, and the forest under-story is dominated by young beeches. 

Common Loon on Black Pond at the Paul Smiths VIC (26 May 2015)
Residential Development and Wildlife in the Adirondacks: Lake-shore development threatens the continued health of the Common Loon. Common Loon on Black Pond at the Paul Smiths VIC (26 May 2015).

Recreation and Residential Development: Recreation and residential development  present another threat to the recovering Adirondack wilderness.  

  • The Adirondack Park has seen large increases in residential development over the last several decades, primarily for second home construction.  Between 1990 and 2004, over 13,500 new houses were permitted in the Park. Between 2005 and 2006, an additional 1,500 were added. Development and its associated loss of habitat poses a threat to the biological diversity of the Adirondacks by fragmenting forest systems and degrading water quality, New housing means new roads, driveways, power and water lines, leach fields, pets, invasive species, and other disruptions to the forest. Highly visible houses on hilltops and lake shores change the aesthetic character of the Park.  The impact of increased residential development on wildlife depends in part on the pattern of development; clustering of development can help mitigate the impact of development on wildlife.  For instance, a 2014 study on the effects of lake-shore development on the reproductive success of Common Loons revealed that the clustering homes on one part of a lake to create buffers allows Common Loons to nest a distance away from developed areas, improving their reproductive success.
  • Recreational uses of the Park also pose threats to the ecosystem. Recreational activities represent a leading factor in endangerment of plant and animal species.  Negative effects on animals include decreased species diversity and decreased survival.  While all recreational activity in the wilderness (even non-motorized and seemingly benign activities such as hiking and birdwatching) disrupt the environment to some degree, recreation involving motorized vehicles – all-terrain vehicles, snowmobiles, and motorized watercraft – is particularly damaging, involving not just disturbance of wildlife, but noise pollution, soil loss, vegetation disturbance, and spread of invasive species.  
Adirondack Wetlands: Bloomingdale Bog.  18 September 2015
Climate Change and the Adirondack Wetlands: Wetlands and the unique plant and animal species which dwell in them are particularly vulnerable to climate change. Bloomingdale Bog (18 September 2015).

Climate Change:  Perhaps the greatest long-term threat to the Adirondack Mountains is climate change.  The Adirondack Park represents a transition zone between the temperate forests to the south and the boreal, spruce-fir forest of Canada. Many of the plant and animal species that have flourished here are at the southern end of their range. This means that Adirondack forests and the species dependent on them, are particularly vulnerable to warming temperatures.

Temperature and weather shifts associated with climate change have already occurred, as the Adirondack weather becomes warmer and wilder.  The Adirondack climate has warmed by about two degrees (Fahrenheit) over the last century.  Warming has changed the timing of ice cover on some lakes, with ice forming later and melting earlier. For instance, on Mirror Lake in Lake Placid, by 2005, ice was forming 14 to 15 days later and melting 3 to 4 days earlier than it had done in the early 1900s. 

Shrubs of the Adirondack Wetland: Bog Laurel on Barnum Bog (31 May 2014)
Climate Change and the Adirondack Wetlands: Lowland boreal plants, like the Bog Laurel, are at risk from warming temperatures. Bog Laurel on Barnum Bog (31 May 2014).

The temperature changes of the past few decades have already affected some species.  For instance, a comparison of bird surveys conducted on Whiteface Mountain in 2013 and 2014 with analogous surveys forty years earlier revealed that many bird species have moved up in elevation, probably in response to rising temperatures.  However, exploring the link between warming and species decline is complicated, because some of the changes documented in the last few decades have many different, interconnected causes. There is evidence, for instance, of a decline in the wetlands occupied by selected boreal bird species (such as Boreal Chickadee, Olive-sided Flycatcher and Rusty Blackbird). However, this development may be due to other factors, such as development and recreation, such as increased development and recreation, working in combination with changing climate.   

Boreal Birds of the Adirondack Wetland: Lincoln's Sparrow on Bloomingdale Bog (5 July 2014).
Climate Change and the Adirondack Wetlands: Shrinking wetlands will reduce suitable breeding habitat for migratory birds such as the Lincoln's Sparrow. Lincoln's Sparrow on Barnum Bog (5 July 2014).

More striking shifts in the forests and wildlife of the Adirondacks will emerge in the coming decades, if (as projected) the warming trend continues.  Even a best-case scenario projects a three to six degree increase in temperature by the 2080s.  As the Park warms, spruce-fir forests will significantly decrease in the Adirondacks, and the boreal birds that dwell in this habitat also will decline.  As boreal birds disappear from the Park, southern birds are expected to move in. The Carolina Wren, Tufted Titmouse, and Mockingbird have been observed in the Adirondacks in greater numbers than previously.  As temperatures rise, non-native species that cannot survive the current Adirondack winters will likely replace native plants and animals.  A shorter ice season for Adirondack lakes could alter lake ecology, making the lakes less suitable for cold-water species such as brook trout and lake trout.


References

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