Publications (currently under construction and updating)

2002
Ayres DR, Strong DR. 2002. The Spartina invasion of San Francisco Bay. Aquatic Nuisance Species Digest 4 (4): 37-38.
2003
Blum MJ, Sloop CM, Ayres DR, Strong DR. In press. Characterization of microsatellite loci in Spartina species (Poaceae). Molecular Ecology Notes (in press)
In preparation:
"Spartina alterniflora-foliosa hybrid invasion alters wetland ecosystems in south San Francisco Bay"
1. J. C. Nordby and J. Albertson. Gray fox
predation of endangered California
clapper rail nest. (a note to be submitted to Journal of Wildlife Biology)
- I documented the first known predation of a rail nest by a gray fox so USFWS
would like to publish it as a note.
2. G. R. Guntenspergen and J. C. Nordby. Impacts of invasive plants on
vertebrates of tidal marshes. (will be a chapter in Avian Biology)
- This is a result from the "Vertebrates of Tidal Marshes" symposium I
attended
last October. We are going to focus on Phragmites and Spartina.
3. Rosso, Nordby, et al. Technical paper with application of LIDAR to marshes
and
how it can be used to assess elevation/vegetation for bird studies.
4. Cuddington, Nordby, et al. Sparrow/Wren/Spartina model
1. Molecular assays
to identify plant pathogenic organisms vectored by biological controlagents.
Leader: Heather D
.and
Dino Garcia-Rossi, Melissa Daost, Don StrongSummary: Phytoplasma bacteria could be introduced or spread bythe ophloem-feeding insect
Prokelisia marginata,
contemplated for biocontrol of S. alterniflora in Willapa Bay, Wa.We sequenced the 16S ribosomal RNA (rRNA) gene of the bacterial species that gave positive
results in general PCR tests for phytoplasma. GenBank sequences suggested that the positive
PCR tests were due to the presence of such bacteria as
Pseudomonas, Holomonas, Vibrio, andAcinetobacte
r; we found no molecular or other evidence suggesting phytoplasmas in eitherSpartina
or P. marginata.Progress. Completed.
Mss. Published,
BioControl 47: 487–497, 2002.
2. Allee Effect at the leading edge of
Spartina invasion, ecosystem wide.Leader: Heather D
.and
Caz T., Janie C. , Don S.Summary:
Isolated plants in areas colonized within the last few years set approximately one-tenth the
seed of plants in continuous meadows, colonized decades ago. Furthermore, the small amount of
seed that was set by isolated plants germinated at only one-third the rate of seed set by meadow
plants, indicating the possibility of inbreeding depression when pollen from other genets is
unavailable. Observed generally, at all fronts of the invasion over the 23,000 ha sweep of the
estuary.
Progress: 99% complete.
Mss. to be submitted to Ecology, December 02.
Potential for Self-Defeating Biological Control?
Variation In Herbivore VulnerabilityAmong Invasive
Spartina Genotypes in Willapa Bay.Leader: D. Strong
and
Dino Garcia-Rossi, Nathan RankSummary: Variation among genotypes in tolerance and resistance related traits of
S. alterniflorato
P. marginata in Willapa bay is very high. Plants of some genotypes were killed by the hopperwhile others suffered no damage. Population growth of the hopper varied greatly as well among
cordgrass genotypes. However tolerance and growth were not correlated, meaning that some
genotypes could foster many planthoppers and not suffer from this herbivory. This sets the stage
for natural selection to remove the intolerant genotypes, which would be self defeating biological
control.
Progress. Complete.
Mss. In review, Ecological Applications.
4. Safety testing for introduction of biological control agent
, Willapa Bay.Leader, Fritzi Grevstad
and, D. G. Rossi, R. W. Switzer, M. Wecker, D. Strong
Summary.
P. marginata was capable of completing its life cycle on only S. alterniflora and S.anglica
; it could not do so only any of the tested 19 valuable grasses, cranberry, or gymnospermsof the Willapa. Thus, we found no evidence of risk to nontarget plants in Washington State from
P.marginata.
Progress: Complete
.Mss. in press. BioControl.
5. R-selection of life history traits
in Willapa S. alternifloraLeader: Heather D.
Summary: In the 100 years of the invasion of Willapa Bay, S. alterniflora has been under a
selection regime for rapid reproduction and high dispersal, which is opposite to that in its native
Atlantic habitats. Willapa Bay plants have much higher reproductive effort and that is positively
correlated with a greater risk of death. Furthermore, plants in the invasive population initiate
reproduction both younger and at a smaller size and are much more self-compatible
Progress: 60% complete.
Mss.
6. Life history evolution
and selection for life in an herbivore free environment, S. alterniflorain Willapa Bay.
Leaders: Heather D and Matt Katz
(no order between leaders).Summary: Is there a correlation between r selected characters and those associated with
herbivore free growth in Willapa Bay?
Progress:
Mss.
7. In depth investigation of S .alterniflora resistance
and tolerance to P. marginata in WillapaBay.
Leader: Matt Katz
Summary:
a. Compare variation in derived population in Willapa to that in native range.
b. Coevolution of P. marginata with S. alterniflora, Willapa and native range.
Progress: First year of data on a, b in planning stage.
Mss.
8. Origins of Willapa S. alterniflora
?Leaders: Heather D., Matt K, and June B.
Summary:
a. Using microsatellites, compare provenances from Atlantic with Willapa Bay.
b. Evolution of life history herbivory resistance-tolerance traits in the invasion?
Progress:
a. Underway
b. Planning stage.
Mss.
8. Quantitative models of Allee effect
of Willapa invasion.Leader: Caz Taylor
and
Heather D. Janie C., Fritzi G., Alan H.Summary: Simulation model of growth and spread by seed, 1km
2 showed that the invasion isslowed with no effects on any other quantitative aspect of spread. A second result is that the
Allee effect means spread is increased by increase selfing rate. A third result is that the invasion
is rate increases rapidly with increased seedling recruitment. This suggests that control of
seedlings is good strategy for control of spread.
Progress: Oral presentation won award for best “Theory: poster at ESA meetings, Tucson.
9. Non-linear matrix model spread.
Leader: Caz Taylor
and
Alan H.Summary:
10. Stochastic model of spread, Bay wide.
Leader: Caz T.
and Alan H.
Summary:
a. Accommodating effect of environmental variation upon parameters of spread.
Idea: Is the invasion pulsed, is seedset and recruitment episodic, perhaps by driven by ENSO
events in temperature and rainfall?
b. Informing control strategies: “nascent foci” line of argument.
Progress: Underway.
11. Ergot on S. alterniflora in Willapa Bay.
Leader: Alison Fisher.
Summary:
a. Present at very low rates of infection, terrestrial strain only, genetically divers via
RAPD markers.
b. Potential for a control strategy?
12. Demography of S. alterniflora, ecosystem wide
.Leader: John L.
and Don S., Janie C.
Summary: The gamut of evidence suggests discontinuous recruitment of S. alterniflora in
Willapa Bay. We are testing the hypothesis that seedset and seedling recruitment are highly
episodic, perhaps as driven by ENSO variability in temperature and rainfall.
Progress:
a. We have made good progress in establishing a field protocol collecting data on seed set
and seedling recruitment on the largest spatial scale of the invasion, at the scale of the entire Bay.
We have recruitment data for two years and seedset data for one year.
b. We have obtained high resolution aerial photos of plants in flower and have lots of
groundtruth data for these plants in 2002. We are planning the GIS and imaging project that will
test the idea that spectral information in the images indicates seedset.
13. Spartina Wrack effect on native vegetation.
Leader: John L.
and Janie C.
Summary: Have experimental and observational data that wrack changes the relative
composition of longer lived native marsh species and facilitates a suite of more ephemeral
species. We are going to couple this with information from the historical photographic record
about the spatial and temporal distribution of wrack disturbance in the Bay.
14.
Spartina wrack influence on terrestrial invertebrate communities.Leader: John L.
and
Heather D.Summary: Pitfall data on inverts along transects from the wrack into the forest, high and low
wrack areas in winter, spring, mid-summer, fall. Using stable isotopes to track
Spartina use.Progress: Underway.
15. GIS analysis of historical aerial photos of Willapa Bay
.Leader: Janie C
and D. Strong, J. Lambrinos, A. Hastings
Summary: Photos from 1942 through 2000 (10 sample years) have been scanned and examined
for presence of S. alterniflora. After GIS coverages are produced, a regional object class will be
applied to the polygons to extract demographic data on lateral growth rates of individuals,
meadow formation rates, recruitment and the effects of tidal elevation, substrate and bioregion
on these processes. LiDAR bathymetry data has been acquired of Willapa's intertidal zone, and
will be incorporated into the GIS project.
Progress: 1994, 1997 complete; 2000 in final editing. Data from other years in draft format.
LiDAR data is being processed.