Dan Binkley -- Current and Recent Projects
Colorado State University
Department
of Forest, Rangeland, and Watershed Stewardship,
Colorado
Forest Restoration Institute, and
Natural
Resource Ecology Laboratory
Full CV
List of Publications
(including some downloadable Adobe.pdf)
Prospectus on
Graduate Studies
Thoughts on Science,
Ecology, and Forestry
Modestly cool photos
Over the past 25 years, my
students, colleagues and I have worked on a wide range of projects, from natural
forest and soil dynamics in northern Alaska to
ecosystem production in intensively managed Eucalyptus forests in Hawaii
and Brazil.
These original research projects have been joined by many papers and books
emphasizing synthesis of knowledge. The largest share of my current work
deals with the Colorado Forest Restoration Institute,
chartered by Congress to improve the health of forests and reduce the risk of
severe wildfires. Our intensive productivity studies continue in Brazil,
along with various projects run by graduate students.

Syntheses:
Individual
studies in ecology need to be woven together into tapestries to tell larger
stories. Some of the larger stories my colleagues, students and I have woven in
the past 5 yr (see publications
page for older work):
Binkley, D., T. Sisk, C. Chambers, J. Springer, and
W. Block. 2007. The role of old-growth forests in frequent-fire landscapes. Ecology and Society 12(2): 18. [online] URL: http://www.ecologyandsociety.org/vol12/iss2/art18/
Kaufmann, M.D. Binkley, P. Fule, M. Johnson, S.L.
Stephens, and T.W. Swetnam. 2007. Defining
old growth for fire-adapted forests of the western United States. Ecology and Society 12(2): 15. [online] URL: http://www.ecologyandsociety.org/vol12/iss2/art15/
Binkley,
D. 2006. Soils in ecology and ecology in soils. Chapter 10
in: History of Soil Science (B. Warkentin, ed.).
Binkley, D., and O. Menyailo
(eds). 2005. Tree Species Effects on Soils: Implications for
Global Change. NATO Science Series, Springer, Dordrecht.
Binkley, D., and J.L. Stape. 2004. Sustainable
management of Eucalyptus plantations in a changing world. Pp.
11-17 in: Eucalyptus in a Changing World, N. Borralho et al. (editors),
Proceedings of IUFRO Conference, Aveiro 11-15, 2004.
Binkley, D., G.G. Ice, J. Kaye, and C.A. Williams. 2004.
Patterns of Variation in Nitrogen and Phosphorus Concentrations in Forest
Streams of the United States.
Journal of the American Water Association, in press.
Binkley, D., 2004. A hypothesis about the interaction
of tree dominance and stand production through stand development. Forest
Ecology and Management 190:265-271.
Binkley, D., J.L. Stape, and M.G. Ryan. 2004.
Thinking about efficiency of resource use in forests. Forest Ecology and
Management 193:5-17
Yanai, R.D., S.V. Stehman, M.A. Arthur, C.E. Prescott, A.J.
Friedland, T.G. Siccama, and D. Binkley. 2004. Detecting change in
forest floor carbon. Soil Science Society of America Journl 67:1583-1593.
Binkley, D. 2003. Response to: Lessons
from the Sandbox: is unexplained nitrogen real? Ecosystems
5:734-735.
Augusto, L., J. Ranger, D. Binkley, and A. Rothe. 2002.
Impact of some common tree species of European temperate forests on soil
fertility. Annals of Forest Science, 59:233-253.
Rocky Mountains:
--effects of elk on N
cycling. Rocky
Mountain National
Park has extremely high densities of elk in low-elevation
valleys, and the elk have altered the vegetation. In the photo, not only are
the aspen restricted to inside the exclosure, but even the sagebrush is growing
better inside. What are the effects on N cycling? We examined various
components of the N budget in 30 exclosures and adjacent areas. Bottom
line: nitrogen limits vegetation growth whether or not elk browsing is
present, but the elk have not yet had a major effect on N cycling (supported by
USGS).

What’s the aspen
regeneration story around the Rocky
Mountain National
Park?
(funded by USGS) We've done
several systematic surveys of aspen across the Park, in pure stands
and in stands mixed with conifers. Aspen regeneration has been generally
good over the past 120 years, except in areas with excessively high elk
population in the past 30 years. In those portions of the Park, aspen
recruitment is about 85-95% lower than expected from long term trends.
(projects with Tom Stohlgren, USGS/BRD, graduate students Kuni Suzuki
and Margot Kaye).
Was Aldo Leopold right
about the Kaibab deer herd?
A central paradigm in wildlife ecology is that predation is a good thing for
prey species: predation limits the population of the prey, and keeps the prey
from overpopulating and devastating the habitat. This appealing idea was
advocated by Aldo Leopold, and he used the classic story of the Kaibab deer
herd as an illustration. The wolves, lions, and coyotes on the Kaibab Plateau
were decimated by government hunters after the plateau was established as a
game preserve -- and Leopold tells the story that the deer population exploded,
the range was degraded, and the deer population crashed below the level that
could have been sustained with a healthy amount of sustained predation.
We challenged this idea by determining the cohort structure of aspen across the
Plateau. High populations of starving deer should have prevented the
establishment of aspen during the 1920s; if we found a sizable cohort from that
period, Leopold’s story would have to be wrong. Our descriptive and
experimental investigations supported the idea of a major deer explosion in the
1920s – but also a much fuller story of long-term changes on the Plateau:

Spatial patterns in tree growth, resource supply, and
efficiency of resource use. PhD student Suzanne Bird mapped the details of
tree growth and resource use in a 10-ha stand of ponderosa pine in the Manitou
Experimental Forest
near Colorado Springs.
All the trees in this plot have been mapped and measured repeatedly by US
Forest Service personnel (supervised by Wayne
Shepperd). Suzie used field measurements
of soil, litterfall, and light interception to describe the spatial patterns in
growth and resource use -- testing hypotheses about changes in efficiency of
resource use as the supply of resources change.
We also examined patterns in dominance among trees within stands for 140
forests across the Rocky Mountains, finding remarkable differences between
single-species and mixed-species stands, as well as a remarkable lack of
substantial dominance in lodgepole pine forests.
Binkley,
D. 2007.
Age distribution of aspen in Rocky Mountain National Park, USA. Forest
Ecology and Management, in press.
Boyden, S., D.
Binkley, and W. Shepperd. 2005. Spatial and temporal patterns in
structure, regeneration, and mortality of an old-growth
ponderosa pine
forest in the Colorado
Front Range.
Forest Ecology and Management 219:43-55.
Kaye, M.W., D. Binkley, and T.J. Stohlgren.
2005. Long-term impacts of conifer invasion and elk browsing on quaking
aspen forests in the central Rocky Mountains, USA. Ecological
Applications 15:1284-1295.
Schoenecker, K.A., F.J. Singer, R.S.C. Menezes, L.C.
Zeigenfuss, and D. Binkley. 2004. Sustainability of vegetation communities
grazed by elk in Rocky Mountain National Park. Journal of Wildlife
Management 68:835-847.
Binkley, D., F. Singer, M. Kaye, and R. Rochelle.
2003. Influence of elk grazing on soil properties in Rocky Mountain
National Park. Forest Ecology and Management 185:239-245.
Kaye, M.W., T.J. Stohlgren, and D. Binkley.
2003. Aspen structure and variability in Rocky Mountain National Park,
Colorado, USA. Landscape Ecology 18:591-603.
Binkley, D., U. Olsson, R. Rochelle, T. Stohlgren, and N.
Nikolov. 2002. Structure, production and resource use in old-growth
spruce/fir forests in the central Rocky Mountains, USA. Forest Ecology
and Management 172:271-279.
Olsson, U., D. Binkley, and F.W. Smith. 1998.
Nitrogen supply, nitrogen use, and production in an age sequence of lodgepole
pine. Forest Science 44:454-457.
Binkley, D., F.J. Singer, M. Kaye, and R. Rochelle.
2002. Influence of elk grazing in soil and nutrients in Rocky Mountain
National Park. Pp. 75-186 in: Singer, F.J., and L.C. Zeigenfuss
(eds.) Ecological Evaluation of the Abundance and Effects of Elk Herbivory in
Rocky Mountain National Park, Colorado, 1994-1999. US Geological Survey
Open Report #02-208, Ft. Collins.
Schoenecker, K.A., F.J. Singer, R.S.C. Menezes, L.C.
Zeigenfuss, and D. Binkley. 2002. Sustainability of vegetation
communities grazed by elk in Rocky Mountain National Park. Pp. 187-204
in: Singer, F.J., and L.C. Zeigenfuss (eds.) Ecological Evaluation of the
Abundance and Effects of Elk Herbivory in Rocky Mountain National Park,
Colorado, 1994-1999. US Geological Survey Open Report #02-208, Ft.
Collins.
Kaye, M.W., K. Suzuki, D. Binkley, and T. Stohlgren.
2001. Landscape-scale dynamics of aspen in Rocky Mountain National Park,
Colorado. In: Sustaining Aspen in Western Landscapes (W.D.
Shepperd, D. Binkley, D. Bartos, T.J. Stohlgren, and L.G. Eskew, eds.), USDA
Forest Service General Technical Report RMRS-P-18, Ft. Collins.
Shepperd, W.D., D. Binkley, D. Bartos, T.J. Stohlgren, and
L.G. Eskew (eds). 2001. Sustaining Aspen in Western Landscapes (.), USDA Forest
Service General Technical Report RMRS-P-18. 460 pp.
Suzuki, K., H. Suzuki, D. Binkley, and T. Stohlgren.
1999. Aspen regeneration in the Colorado Front Range: differences
at local and landscape scales. Landscape Ecology 14:231-237.

Productivity
in fast-growing plantations
-- What controls the peak of
stand production with age, and why does it decline while the trees are still
young and vigorous? (Sponsored by NSF, and 8 companies
in Brazil)
The old answer of increasing respiration cost of maintaining big trees has been
largely discounted by data and modeling. In Hawaii we established stands of 2 densities
(to vary the ratio between leaf area and wood biomass/tree) and three
fertilization regimes, and have been following the entire carbon C budget in 18
plots. We essentially disproved all our original ideas, finding that gross
primary production declined in older periods despite sustained high use of
water, light and nutrients. This led to a series of more ambitious
projects in Brazil
that included testing aspects of genetics, stand structure, and resource
supply.


We've also done extensive
work comparing replicated plantations of Eucalyptus
and N-fixing Albizia.
The greater wood production by the Eucalyptus
trees results in part from greater total productivity (NPP), and in part from
greater allocation of production aboveground.

This project involves
intensive soil experiments, including changes in soil C. The prior land use was
sugar cane cropping, and the C4 signature on the "old" soil C allows
us to examine both the loss of "old" soil C and gain of new C3 carbon
from the Eucalyptus.
After 8 years, the total soil C had not changed, but there was a significant
loss of old C, and a significant gain of new C. Intriguingly, addition of
massive amounts of fertilizer N did not alter the gain of new C or loss of old
C -- exactly unlike our findings for N fixation!


We started a new project in Hawaii in 1999 (NSF
support): We harvested 18-yr-old plantations of Eucalyptus and Albizia, and used
reciprocal plantings to examine the second-rotation legacy of the
first-rotation species, including fertilization treatments to try and modify
the legacy. The project is a collaboration between the University
of Hawaii in Hilo (a traditional undergraduate institution
with a large minority enrollment), CSU, and the USDA Forest Service. Randy
Senock at UHH is the leader, with collaborators including: Bob
Powers and Matt
Busse of the Forest Service, and Thais Winsome from UC Davis. This second
rotation will be complete in the summer of 2008, when we’ll assess the overall
outcome of the experiment. .
Brazil: Prof. Jose Luis Stape at the University
of Sao Paulo in Piracicaba, Brazil
is leading several sets of great studies on factors controlling growth of Eucalyptus
plantations. Mike Ryan (USDA Forest Service, Rocky Mountain Research
Station) and I are collaborating with Stape.
Clonal plantations are much more uniform in structure (left side of
photo) than seedling-origin stands (right side of photo), and we're using this
uniformity to examine a single-tree/stand-structure hypothesis for age-related
declines in stand growth.

We started a series of
plantation projects in Brazil in 2001, and followed the complete carbon budget
for an entire rotation, examining the importance of genetics (clones vs.
seedlings), stand structure (uniform clonal-origin trees vs. same genotype but
with more diversity of tree sizes within plots), water supply and nutrient
supply. Eight companies (VCP, Aracruz, International Paper, Veracel,
Copener, CENIBRA, Suzano-Bahia Sul, and Vallourec Mannesmann) are participating
in the Brazil Eucalyputs Potential Productivity (BEPP) Project. We’ll be hosting an international conference
on productivity in tropical tree plantations in Porto Seguro, Brazil, in
October 2008. (http://lamar.colostate.edu/~binkley/Brazileucalyptus.htm;
Stape pictured at left in
2 yr old stand .

Binkley, D., J.L. Stape, E.N Takahashi, and M.G.
Ryan. 2006. Tree-girdling to separate root and heterotrophic
respiration in two Eucalyptus stands in Brazil. Oecologia
148:447-454.
Stape, J.L., D. Binkley,
W.S. Jacob, and E.N. Takahashi. 2006. A twin-plot approach to determine
nutrient limitation and potential productivity in Eucalyptus plantations at landscape
scales in Brazil. Forest Ecology and Management 223:358-362.
Boyden, S., D. Binkley, and R. Senock. 2005.
Competition and facilitation between Eucalyptus and nitrogen-fixing Falcataria
in relation to soil fertility. Ecology 86:992-1001.
Stape, J.L., D. Binkley, M.G. Ryan, and A.N. Gomes.
2004. Water use, water limitation, and water use efficiency in a Eucalyptus
plantation. Bosque 25:35-41.
Binkley, D., and J.L. Stape. 2004. Sustainable
management of Eucalyptus plantations in a changing world. Pp.
11-17 in: Eucalyptus in a Changing World, N. Borralho et al. (editors),
Proceedings of IUFRO Conference, Aveiro 11-15, 2004.
Binkley, D., J.L. Stape, and M.G. Ryan. 2004. Thinking
about efficiency of resource use in forests. Forest Ecology and
Management 193:5-16.
Stape, J.L, M.G. Ryan, and D. Binkley. 2004.
Testing the 3-PG process-based model to simulate Eucalyptus growth with an
objective approach to the soil fertility rating parameter. Forest Ecology
and Management 193:219-234.
Stape, J.L., D. Binkley, and M.G. Ryan. 2004.
Eucalyptus production and the supply, use and the efficiency of use of water,
light and nitrogen across a geographic gradient in Brazil. Forest Ecology
and Management 193:17-31.
Ryan, M.G., D. Binkley, J. Fownes, C. Giardina, and R.
Senock. 2004. An experimental test of the causes of age-related decline
in forest growth. Ecological Monographs 74:393-414.
Binkley, D., J. Kaye, M. Barry, and M.G. Ryan.
2004. First-rotation changes in soil carbon and nitrogen in a Eucalyptus
plantation in Hawaii. Soil Science Society of America Journal
68:1713-1719.
Giardina, G.P., D. Binkley, M.G. Ryan, and J.H. Fownes.
2004. Fertilization decreases belowground carbon cycling in a humid
tropical forest. Oecologia 139:545-550.
Binkley, D., J.L. Stape, and M.G. Ryan. 2004.
Thinking about efficiency of resource use in forests. Forest Ecology and
Management 193:5-17.
Binkley, D., R. Senock, and K. Cromack, Jr.
2004. Phosphorus limitation on nitrogen fixation by Falcataria
seedlings. Forest Ecology and Management 186:171-176.
Giardina, C., M.G. Ryan, D. Binkley, and J. Fownes. 2003.
Primary production and C allocation in relation to nutrient supply in an
experimental tropical forest. Global Change Biology, in press.
Binkley, D., R. Senock, S. Bird, and T.G. Cole.
2003. Twenty years of stand developement in pure and mixed stands of
Eucalyptus saligna and nitrogen-fixing Facaltaria mollucana. Forest
Ecology and Management 182:93-102.
Binkley, D., M.G. Ryan, J.L. Stape, H. Barnard, and J.
Fownes. 2002. Age-related decline in forest ecosystem growth: an
individual-tree, stand-structure hypothesis. Ecosystems 5:58-67.
Resh, S., D. Binkley, and J. Parrotta. 2002.
Greater soil carbon sequestration under nitrogen-fixing trees compared with
Eucalyptus species. Ecosystems 5:217-231.
Binkley, D., C. Giardina, and M. Bashkin. 2000. Soil
phosphorus pools and supply under the influence of Eucalyptus saligna and
nitrogen-fixing Albizia facaltaria. Forest Ecology and Management, 128:241-247.
Kaye, J.P., S.C. Resh, M.W. Kaye, and R.A. Chimner.
2000. Nutrient and carbon dynamics in a replacement series of Eucalyptus
and Albizia trees. Ecology 81:3267-3273.
Binkley, D., and S. Resh. 1999. Rapid changes in
soils following Eucalyptus afforestation in Hawaii. Soil Science Society of
America Journal 63:222-225.
Binkley, D., and M. Ryan. 1998. Net primary
production and nutrient cycling in replicated stands of Eucalyptus saligna and
Albizia facaltaria. Forest Ecology and Management 112:79-85.
Garcia-Montiel, D.C., and D. Binkley. 1998. Effect of
Eucalyptus saligna and Albizia falcataria on soil processes and nitrogen supply
in Hawaii. Oecologia 113:547-556.
Binkley, D., and C. Giardina. 1998. Why
trees affect soils in temperate and tropical forests: the warp and woof of
tree/soil interactions. Biogeochemistry 42:89-106.
Bashkin, M.A., and D. Binkley. 1998. Changes in
soil carbon following afforestation in Hawaii. Ecology 79:828-833.
Binkley, D. 1997. Bioassays of the influence of
Eucalyptus saligna and Albizia falcataria on soil nutrient supply and limitation.
Forest Ecology and Management 91:229-234.
Rhoades, C., and D. Binkley. 1996. Factors
influencing decline in soil pH in Hawaiian Eucalyptus and Albizia
plantations. Forest Ecology and Management 80:47-56.
Ewers, B., D. Binkley, and M. Bashkin. 1996.
Influence of adjacent stand on spatial patterns of carbon and nitrogen in
Eucalyptus and Albizia plantations. Canadian Journal of Forest Research
26:1501-1503.
Zou, X., D. Binkley, and B. Caldwell. 1995.
Effects of dinitrogen‑fixing trees on phosphorus biogeochemical cycling
in contrasting forests. Soil Science Society of America Journal 59:1452-1458.
Binkley, D., K.A. Dunkin, D. DeBell and M.G. Ryan.
1992. Production and nutrient cycling in mixed plantations of Eucalyptus
and Albizia in Hawaii. Forest Science 38:393-408.