Research Interests

"In the woods, too, a man casts off his years, as the snake his slough, and at what period soever of life, is always a child. ...In this wood, we return to reason and faith."    -Ralph Waldo Emerson


Research Interests:

I study the ecology of forest communities, especially ecosystems of conservation concern. My research focuses on the dynamics of these communities and the role of natural disturbance and human-caused disturbance. Generally, my goal is to reach conclusions that will aid in the conservation or restoration of native species and ecosystems. Currently, I'm working on three projects: fire ecology in the Chiricahua Mountains in southeastern Arizona (Arizona fire ecology research), the dynamics of jack pine on GreatWass Island, Maine (Jack pine on Great Wass Island), and invasive plants in the Farmington area (Farmington Invasive Plants).

Don't miss the section a the bottom on Research Opportunities for Students on my projects!!!


Arizona fire ecology research:

I've worked on several projects over the last few years on the fire ecology of pine and pine-oak forests in the Chiricahua Mountains in southeastern Arizona.  For information on completed projects, see Recent Publications.  Below, I provide an abstract for a recent talk I gave that synthesizes parts of my fire ecology over the last 12 years or so.  The second abstract is from a recent collaborative project with Tom Swetnam and Chris Baisan at the Laboratory of Tree-Ring Research at the University of Arizona, is an attempt to disentagle the roles of fire and drought severity in the dynamics of Arizona pine in two adjacent sites that exhibit very similar environments but divergent fire histories.  I've provided a couple abstracts from recent publications and presentations.  My current Arizona fire ecology research is on Arizona madrone and understanding the combined effects of crown fire and drought on pine regeneration.


Barton, A.M.  “Madrean pine-oak forests in Arizona: past dynamics, present problems.”  Wildlife Society and Association for Fire Ecology Conference on Managing Fire and Fuels in the Remaining Wildlands and Open Spaces of the Southwestern United States, December 2-5, 2002, San Diego, California.
This paper synthesizes research on presettlement dynamics and modern disruption of Madrean pine-oak forests in Arizona. In response to low-severity fires characteristic of presettlement, pines were fire resistant, exhibiting high top-survival, whereas oaks were fire resilient, exhibiting low top-survival but pronounced resprouting. Thus, low-severity fire favors pines, but resprouting allows oaks to rebound during inter-fire periods. Age structures reveal large increases in stand density as a result of modern fire suppression, suggesting much more open conditions and a higher pine:oak ratio during presettlement times. Fires were, in fact, so frequent that fire-caused thinning rarely stimulated radial growth. In anomalous high-severity crown fires, seedling establishment was very low for pines and oaks, but most oaks resprouted. P. leiophylla also resprouted but at low levels, which might nonetheless be an important source of future pines. These results suggest that anomalous high-severity fires can transform Madrean pine-oak forests into more homogenous oak woodlands. This synthesis argues for the urgency of restoration using a variety of flexible approaches.


Barton, A.M., T.W. Swetnam, and C.H. Baisan.  2001 Arizona pine (Pinus arizonica) stand dynamics: local and regional factors in a fire-prone madrean gallery forest of Southeast Arizona, USA.  Landscape Ecology 16: 351-369
In southwestern North America, large-scale climate patterns appear to exert control on moisture availability, fire occurrence, and tree demography, raising the compelling possibility of regional synchronization of forest dynamics.  Such regional signals may be obscured, however, by local, site-specific factors, such as disturbance history and land use.  Contiguous sites with similar physical environments, lower and middle Rhyolite Canyon, Arizona, shared nearly the same fire history from 1660-1801, but then diverged.  We related stand dynamics of Arizona pine (Pinus arizonica) to fire history and drought severity and compared the dynamics in the two sites before and after the divergence in fire frequency.  Fires occurred during unusually dry years, and possibly following unusually moist years. Arizona pine exhibited three age structure peaks: two (1810-1830 and 1870-1900) shared by the two sites and one (1610-1640) only in middle Rhyolite.  The latter two peaks occurred during periods of unusually low fire frequency, suggesting that fire-induced mortality shapes age structure.  Evidence was mixed for the role of favorable moisture availability in age structure.  As expected, moisture availability had a prominent positive effect on radial growth, but the effect of fire was largely neutral. The two sites differed only moderately in stand dynamics during the period of divergence, exhibiting subtle age structure contrasts and, in middle Rhyolite only, reduced growth during a 49-year fire hiatus followed by fire-induced release.  These results suggest that, despite local differences in disturbance history, forest responses to regional fire and climate processes can persist.

 
 
 

Jack pine on Great Wass Island:

The research project on the ecology of jack pine woodlands on Great Wass Island as a collaboration with students.  Jack pine is a northern species that reaches the southeastern limit of its distribution in the Downeast area of Maine. Great Wass Island has one of the largest populations of jack pine in Maine, as well as many rare plants and ecosystems.  Jack pine is typically a fire-dependent species that is replaced by more shade tolerant species (e.g., spruce) in the absence of fire.  It also is typically a species of dry sandy soils or outcrops.  Surprisingly, there's very little evidence of fire on Great Wass Island over the past century.  Also puzzling is that large stands of jack pine occur in wet peat bogs.  We are using a combination of tree-ring analysis and aerial photographic analysis to address several questions: (1) how has jack pine persisted on the island without fire, (2) has jack pine invaded bogs only in the past century, and (3) what drives the waves of regeneration (short periods over the last century during which this species has established many new individuals) apparent in our data on jack pine ages.  I've provided two abstracts from recent presentations by students on this work.  Dan Grenier and I are (as of spring 2004) completing the cross dating of cores for this project.
    Recently, I submitted a grant proposal (with Julia Daly of UMF and Ann Dieffenbacher-Krall and George Jacobson of UM Orono) to the National Geographic Society to extend work to the paleoecology of the bogs.  An abstract from that proposal is provided below.

Ten students have worked with me on the project so far, and it has been a great success and lots of fun.  The abstracts below, from the Spring 2000 UMF symposium, should provide an ideas of the range of projects we're pursuing.   See below for student research opportunities on this project.
 

Dan Grenier.  Jack pine in the absence of fire on Great Wass Island, ME: bog and outcrop populations
We investigated the population dynamics of jack pine on rock outcrops and in bogs at the southeastern margin of its distribution, in mid-coast Maine.  Jack pine is typically a fire-dependent species, which is replaced by more shade-tolerant species, such as spruce, in the absence of fire.  Using analyses of age structure and seedling establishment, we assessed whether jack pine is self-perpetuating on Great Wass Island, where there is little evidence of past fire.  The stands generally exhibit patterns indicating self-perpetuating populations, although clear pulses of recruitment synchronized among sites are also apparent, especially in outcrop stands.  Factors other than fire, such as climatic fluctuations, are most likely to account for these pulses.  Compared to outcrops, bogs tend to have relatively young populations with vigorous trees and many seedlings.  These results suggest recent invasion of bogs by jack pine, perhaps as a result of bog succession or climate fluctuations.  This is the first documentation of bog populations of this species, although this has been found for similar fire-associated, stress-tolerant pines.

Max Postvanderburg and Stasia Savasuk.  Invasion of bogs on Great Wass Island by Jack Pine: an aerial photographic analysis
The Great Wass Island Project, led by Dr. Andrew Barton, has documented, for the first time, the occurrence of jack pine in bogs.  This is unusual given that jack pine typically grows on dry soils subject to frequent fire, both of which are not characteristic of Great Wass Island. Results from age structure analyses suggest that jack pine invaded these bogs in the 20th century, whereas those portions of the population occurring on outcrop sites appear to be much older.  We are attempting to test this hypothesis by using aerial photographs, which exist for much of the US from before 1950 to the present. After intensive searching, we found and obtained aerial photographs for three dates: 1996, 1975, and 1940. Using three bog sites for which age structure data now exist, we will be comparing the three photos to examine the extent of invasion of jack pine and other tree species over a 56-year period (1940 to 1996). We will describe our analytical methods, preliminary results, and future projects that may aid in understanding jack pine population patterns on Great Wass Island.
 

Andrew M. Barton, Julia F. Daley, Ann C. Dieffenbacher-Krall, and George L. Jacobson.  Paleohistory of Disjunct Plants and Fire in Coastal Plateau Bogs on Great Wass Island, Maine.  Summary of Grant Proposal Submitted in 2004.
The eastern coast of Maine is botanically distinct from the rest of the state.  The cool, maritime climate harbors a unique assemblage of rare and disjunct northern flora, especially in coastal plateau bogs, a peatland-type confined to a short stretch of the far eastern coast.  Great Wass Island supports the largest area of these bogs as well as an extensive disjunct stand of Pinus banksiana at its southeastern geographic limit.  Recent work has revealed that P. banksiana, a species usually confined to xeric sites, began invading coastal plateau bogs on the island in the early 20th century.  We propose to address two sets of issues using analyses of fossil pollen, macrofossils, and charcoal in peat cores: (1) the colonization and subsequent dynamics of this unique northern plant assemblage in response to climate since glacial retreat (~13,000 years before present) and (2) the more recent dynamics of P. banksiana in these bogs, in particular whether the recent invasion is part of a fire-driven cycle or a response to recent environmental change.  We will analyze peat cores employing standard techniques, including radiocarbon dating, examination of contiguous 2- to 5-cm intervals, identification of periods of fire activity, pollen recognition at 100- to 200-year resolution, and the use of an extensive reference collection for identification of pollen and macrofossils.  This project would illuminate some fundamental biogeographic and conservation issues regarding the responses of the unique flora of coastal plateau bogs to past climates and fire as well as to ongoing climate alterations.



Farmington Invasive Plants:

This project is a collaboration among Nancy Prentiss (instructor in Natural Sciences, two students (Lauri Brewster and Annie Cox), and myself.  The goal of Phase I of the research, which has now been completed, was to document which  non-native woody invasive plants occurred in the Farmington area and to examine their origin and habitat relationships.  In addition to presentations at UMF by Lauri and Annie, I gave a talk on the work at the fall 2003 New England Invasives Summit in Framingham, MA.  We have an article on the research in press in Biological Invasions (see Recent Publications), and I published a magazine article in Natural New England in winter 2004.  I'm now thinking about the next step in this project.  Below is the Abstract from our in press paper.


Barton, A.M., L. Brewster, A. Cox, and N. Prentiss.  In press.  Nonindigenous invasive woody plants in a rural New England town.  Biological Invasions
We examined the distribution and abundance of non-indigenous woody invasive plants in Farmington, Maine, a rural New England town in a forested landscape.  We found 12 invasive species and more than 7 patches per km from surveys on 33 transects (54.3 km) along field edges, abandoned railroad-right-of-ways, riparian zones, and roadsides.  Invasive abundance was greater than for undeveloped roadsides in a forested landscape in Upstate New York, but apparently lower than for more developed areas of the northeastern U.S., where, in contrast to western Maine, invasives have extensively penetrated forest interiors.  Invasive abundance increased with amount of lawn and proximity to town, suggesting a close association between local horticulture and the spread of woody invasives.  Invasive abundance and diversity were highest in riparian areas, probably due to relatively high levels of propagule pressure.  Species differed in the extent of invasiveness, ranging from those still dependent on planted parent trees to fully invasive populations that had spread well beyond their planted origins.  The invasive species recorded in this study have caused ecological and economic damage elsewhere.  The lower levels of invasiveness in Farmington are likely a result of the isolation, small human population, and forested landscape rather than low levels of invasibility.  This suggests the potential for future risks, and the importance of intervention while populations can still be eradicated or controlled.



Recent Publications:

Barton, A.M., L. Brewster, A. Cox, and N. Prentiss.  In press.  Nonindigenous invasive woody plants in a rural New England town.  Biological Invasions*

Barton, A.M.  In press.  Response of Arbutus arizonica (Arizona Madrone) to the fire in southeastern Arizona.  Southwestern Naturalist.*

Barton, A.M.  In press.  Madrean pine-oak forest in Arizona: past dynamics, present problems.  In Managing Fire and Fuels in the Remaining Wildlands and Open Spaces of the Southwestern United States. USDA Forest General Technical Report PSW-GTR.*

Barton, A.M.  2004.  Invasive plants – Why should we be concerned?  Natural New England Winter 2004: 6-9.

Barton, A.M.  2003.  Review: Trabaud, L. and R. Prodon, editors.  2002.  Fire and Biological Processes.  Quarterly Review of Biology 78: 247-248.

Barton, A.M.  2002.  Liquidation harvesting in Maine: where to from here?  Northern Woodlands Magazine, Winter Issue, pages 46-51.

Barton, A.M.  2002.  Intense wildfire in southeastern Arizona: transformation of a Madrean pine-oak forest to oak woodland.  Forest Ecology and Management 165: 205-212.*

Barton, A.M., T.W. Swetnam, and C.H. Baisan.  2001 Arizona pine (Pinus arizonica) stand dynamics: local and regional factors in a fire-prone madrean gallery forest of Southeast Arizona, USA.  Landscape Ecology 16: 351-369.*

Barton, A.M. 2000.  Book Review: Fire in Ecosystem Management: Shifting the Paradigm from Suppression to Prescription.  Proceedings of the 20th Tall Timbers Fire Ecology Conference.  Quarterly Review of Biology 75:  488-489.

Barton, A.M.  1999. Pines versus oaks: effects of fire on the composition of Madrean forests in Arizona.  Forest Ecology and Management 120: 143-156.*

Barton, A.M. and M.D. Wallenstein.  1997.  Effects of invasion of Pinus virginiana on soil properties in serpentine barrens in southeastern Pennsylvania.  Journal of the Torrey Botanical Society 124: 297-305.*

Barton, A. M. and S. K. Gleeson.  1996.  Ecophysiology of oaks and red maple across a topographic gradient in eastern Kentucky.  Forest Science 42: 335-342.*

Barton, A. M.  1995.  Fire resistance vs. post-fire resprouting: differential effects of fire and fire suppression on pine and oak species in Madrean forests in Arizona.   Pages 159-163 in Fire in wilderness and park management: past lessons and future opportunities.  USDA Forest Service, Intermountain Research Station, General Technical Report. INT-GTR-320.

(*Peer reviewed)


 

Research Opportunities for students

Come talk to me about doing ecological research on the forests of Maine. I have found that faculty-student research provides benefits both for the students and for me: I garner incentive, stimulation, collegiality, and physical help for my research program, while students gain confidence, one-on-one attention, an enhanced CV, and a much improved understanding of how science works.

The "Work Initiative" program at UMF has greatly enhanced research opportunities and atmosphere.  Here's how it works.  Professors decide on appropriate faculty-student collaborations for the summer or during the school years, and the university pays students to work on the project (up to $1000 per semester and $2000 during the summer).

I've had about 15 students work with me over the last six years.  Some, usually younger students, have acted as assistants to older students and to me.  As students gain more experience, they take on more responsibility and independence.  Students have given talks at national scientific meetings and co-authored a paper with me published in a peer-reviewed scientific journal.  I've also had students work with me on "green campus" projects, such as the successful effort to design the new UMF Education Building as a green, environmentally sensitive building.

Projects that students could work on in 2004-2005 are the following:
(1) Invasives plants in the Farmington area,
(2) Peat coring and pollen analysis on Great Wass Island (if we get funding), and
(3) Green campus projects, especially focusing on carbon dioxide emissions and energy conservation.

Come by, call, or email me to talk about opportunities for you.
 
 

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