Christa P.
H. Mulder

Chair, Department of Biology and
Wildlife
and
Associate Professor in Ecology
Institute of Arctic Biology
University of Alaska Fairbanks,
Fairbanks, AK 99775, USA
Email cpmulder@alaska.edu
Tel: +1 (907) 474 5493; Fax: +1
(907) 474 6769
Office: Irving I rm 212
Teaching: courses and resources
Public Outreach
Department
of Biology and Wildlife
Note: some projects include several of these themes.
Non-native plant species have been
expanding rapidly across the state of Alaska, likely aided by higher winter
temperatures and long growing seasons, increased levels of human traffic, and
more frequent and larger wildfires. Several projects evaluate the impacts of
changes in abundance of introduced plant species on plant communities:
Are Alaskan Pollinators Abandoning Native Berries for an Exotic
Clover? Implications for Invasive Plant Management on Fruit Production. In this
project we evaluate whether and how the expansion of non-native Melilotus alba
across the state of Alaska affects pollination and fruit set of two berry
species: Vaccinium vitis-idaea
(bog cranberry) and Vaccinium uliginosum (bog blueberry). This is a
collaboration with Matt Carlson
(UA Anchorage).




Non-native
Melilotus alba (plant with white flowers) in
recently burned forest (with grad student Katie Villano
Spellman); tagging cranberries; a prolifically flowering cranberry; testing germination
of non-natives in the soil from different habitats
What
factors affect the success of invasive plants in natural environments? Recently
burned forest is likely to be particularly susceptible to invasion, and forest
fires are increasing in both frequency and extent. Projects associated with
this question include:
§ Greenhouse
experiments conducted by Katie Villano (former MS
student) to evaluate soil and ground cover factors that best explained
germination and growth of three introduced plant species, and by Luke Ponchione (former undergraduate student) to evaluate the
role of moss species in facilitating or retarding the germination of introduced
plant species.
§ A survey
of burned habitat along four roads in interior Alaska to establish a baseline for
the distribution and abundance of non-native plants. Click here to link to the
technical report that resulted from this.
Climate change in northern environments: direct and indirect
effects on plant communities
Arctic and subarctic communities are subjected to some of the fastest
rates of climate change on the planet. To what extent are impacts on plant
communities driven by direct effects (e.g., changes in temperature and
precipitation) and to what extent are they driven by changes in interactions
with other organisms, such as herbivores or pollinators? How important are
changes in winter vs. summer conditions? Several projects fall under this
theme:
·
Cold Sick Plant Project: This is a collaboration between my lab and
that of Bitty Roy (U.
of Oregon). We are investigating changes in attack rates by plant
herbivores and pathogens on understory species in boreal forest to answer the question:
does environmental variation affect herbivores and pathogens primarily
directly, or primarily through changes in plant qualities? See
Mulder et al. 2008.
·
Pathogens on alders: Jenny Rohrs-Richey (Ph.D. 2011) evaluated the role of drought
stress in affecting the susceptibility of alder
(Alnus fruticosa)
to a canker (Valsa melanodiscus).
For more, see Rohrs-Richey et al. 2011.





Working in the rain; Jenny Rorhs-Richey (PhD
student) downloading dataloggers; a plant pathogen on
cranberry; a leaf roller on alder; Christa at a site destroyed by a forest
fire; habitat degradation from goose grubbing and flooding at La Pérouse Bay
Plant phenology, climate change, and geese in
a subarctic saltmarsh: this is a new collaboration with R.F. Rockwell (American Museum of
Natural History), and David
Koons and Lise Aubry (Utah
State). We are evaluating how different aspects of climate change affect plant
phenology, whether we can predict how different plant species will respond, and
how shifts in plant phenology will affect snow goose populations. See Hudson Bay Project for more
information on this habitat.
Other publications on this theme include Wipf et al. 2006 and Rixen and Mulder 2009.
Impacts of seabirds on plant communities.
Seabird
islands are islands that have high populations of seabirds. They are often remote
and in many cases lack the predators found on the mainland or islands closer to
the mainland. Seabird islands occur worldwide and they are of high conservation
value because they often have very high levels of endemism and may serve as
“safe havens” for species that are rare or no longer present on the mainland.
However, many of the islands have been invaded by non-native predators such as
rats, cats, and foxes, with devastating effects for native bird, reptile and
mammal populations. Restoration of hundreds of islands has focused on the
removal of these predators, but little attention has been paid to other aspects
of restoration beyond monitoring seabird populations.






Aorangaia island (Poor Knights, New Zealand); moving carefully across
burrow-riddled ground; close-up of seabird burrows; decomposing leaves marked
while on the tree; graduate students Mel Durrett and
Nikki Grant-Hoffman on New Zealand islands
SEAPRE (Seabird Islands and Introduced
Predators: Impacts of Presence and Eradication on Island Function): I was the Principal Coordinator of this Research Coordination
Network, which brought together people from across the world for cross-system
comparisons and synthesis of the impacts of seabirds and introduced seabird
predators on island ecology, with the further aim of improving restoration
plans for islands on which these introduced predators have been or are being
eradicated. The main product from this network was a book: Seabird Islands: Ecology, Invasion, and Restoration,
published by Oxford University Press in 2011.
RASP (Rats and Islands Project). In this project, run in collaboration with Manaaki
Whenua - Landcare Research
and Department of Conservation (both of New Zealand) examined the effects of
invasive rats on vegetation and soils, both directly (e.g. through changes in
seed or seedling consumption) and indirectly (by reducing or eradicating
seabird populations). For more details, see Fukami et al. 2006, Wardle
et al. 2007, Mulder
et al. 2009, Towns et
al. 2009, Bellingham
et al. 2010, Grant-Hoffman
et al. 2010a, Grant-Hoffman
et al. 2010b.
Additional information:
Members
of the Mulder lab
Publications
Teaching Public Outreach
Mulder c.v. (as pdf file)