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Whitcraft,
C.R. and B.J. Grewell. 2011 online.
Managing perennial pepperweed (Lepidium
latifolium) in a seasonal
wetland prior to restoration of tidal
hydrology. Wetland
Ecology and
Management
(available as pdf soon)
Whitcraft,
C.R., B.J.
Grewell, and P. Baye*. 2011 online. Estuarine
vegetation at Rush Ranch, San Francisco
Bay National Estuarine Research Reserve,
California. San
Francisco Estuary and Watershed
Science (available as pdf
soon) *all authors contributed equally
Whitcraft, C., L. Levin, D.
Talley,
and J. Crooks. 2008. Utilization of invasive
tamarisk by salt marsh
consumers. Oecologia. (abstract) (.pdf)
Whitcraft, C. R. & L.
Levin.
2007. Regulation of benthic algal and animal
communities by salt marsh
plants: impact of shading. Ecology
88(4): 904–917. (abstract)
(.pdf)
Whitcraft, C. R., D. Talley,
J.
Crooks, J. Boland, and J. Gaskin. 2007.
Invasion of tamarisk (Tamarix spp.)
in a southern California salt marsh. Biological
Invasions 9(7): 875-879. (abstract) (.pdf)
Whitcraft, C.R. and L.F.
Pierotti.
Submitted. Trophic roles of an ephemeral
seagrass, Ruppia maritima,
in
a southern California lagoon.
Whitcraft, C., L. Levin, D.
Talley,
and J. Crooks. In prep. “Terrestrialization”
of coastal wetland
ecosystems by a riparian invader.
Levin, L.A., C. R. Whitcraft,
P.
Lamont, G. Cowie, and G. Mendoza. Accepted
pending revision. Response
of biota and bioturbation to oxygen gradients
within the lower oxygen
minimum zone: A high-resolution view of the
Pakistan margin 700-1100 m. Deep Sea
Research II: 56 (6-7): 449-471
(.pdf)
Gooday, A.J., L.A. Levin, A. Aranda da Silva,
B.J.
Bett, G.L. Cowie, J.D. Gage, D.J.
Hughes, R. Jeffreys, P.A.
Lamont, K.A. Larkin, S.J. Murty, S.
Schumacher, C. Whitcraft,
and C. Woulds. 2009. Faunal responses to
oxygen
gradients on the Pakistan margin: a comparison
of foraminifera,
macrofauna and megafauna. Deep
Sea Research
II 56 (6-7): 488-502.
(.pdf)
Woulds, C., G. Cowie, L. Levin, H. Andersson,
J.
Middelburg, S. Vandewiele, P. Lamont, K.
Larkin, A. Gooday, S.
Schumacher, C. Whitcraft, R.
Jeffreys, and M.
Schwartz. 2007. The role of sea floor
biological communities in
sedimentary carbon cycling: oxygen and other
controls. Limnology
and Oceanography 52(4): 1698-1709. (abstract)
(.pdf)
Collinetti, E., W. Miller, K. Lion, A.
Arnwine, B.
Wells, C. Whitcraft, G M.
Ruiz. Smithsonian
Environmental Research Center (SERC) Marine
Invasion Research
Laboratory - Results from the National Ballast
Water Information
Clearinghouse. http://massbay.mit.edu/resources/pdf/MarinePDF/2001/MBI2001abs2.pdf
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Whitcraft, C.,
L. Levin, D. Talley,
and J. Crooks. 2008. Utilization of invasive
tamarisk by salt marsh
consumers. Oecologia.
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Plant invasions of coastal wetlands are rapidly
changing
the structure and function of these systems
globally. Alteration
of litter dynamics represents one of the
fundamental impacts of an
invasive plant on salt marsh ecosystems. Tamarisk
species (Tamarix
spp.), which extensively invade terrestrial and
riparian habitats, have
been demonstrated to enter food webs in these
ecosystems.
However, the trophic impacts of the relatively new
invasion of tamarisk
into marine ecosystem have not been assessed.
We evaluated the
trophic consequences of invasion by tamarisk for
detrital food chains
in the Tijuana River National Estuarine Research
Reserve salt marsh
using litter dynamics techniques and stable
isotope enrichment
experiments. The observations of a short
residence time for
tamarisk combined with relatively low C:N values
indicate that tamarisk
is a relatively available and labile food source.
With an isotopic
(15N) enrichment of tamarisk, we demonstrated that
numerous
macroinvertebrate taxonomic and trophic groups,
both within and on the
sediment, utilized 15N derived from labeled
tamarisk detritus. Infaunal
invertebrate species that took up no or limited
15N from labeled
tamarisk (A. californica, enchytraeid
oligochaetes, coleopteran larvae)
occurred in lower abundance in the tamarisk
invaded environment. In
contrast, species that utilized significant 15N
from the labeled
tamarisk, such as psychodid insects, an exotic
amphipod, and an oniscid
isopod, either did not change or occurred in
higher abundance. Our
research supports the hypothesis that invasive
species can alter the
trophic structure of an environment through
addition of detritus and
can also potentially impact higher trophic levels
by shifting dominance
within the invertebrate community to species not
widely consumed. 
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| Whitcraft, C. R. & L. Levin.
2007. Regulation of benthic algal and animal
communities by salt marsh
plants: impact of shading. Ecology
88(4): 904–917. |
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Plant cover is a fundamental feature of many
coastal
marine and terrestrial systems and controls the
structure of associated
animal communities. Both natural and
human-mediated changes in
plant cover influence abiotic sediment properties
and thus have
cascading impacts on the biotic community. Using
clipping (structural)
and light (shading) manipulations in two salt
marsh vegetation zones
(one dominated by Spartina foliosa and one by
Salicornia virginica), we
tested whether these plant species exert influence
on abiotic
environmental factors and examined the mechanisms
by which these
changes regulate thebiotic community. In an
unshaded (plant and shade
removal) treatment, marsh soils exhibited harsher
physical properties,
a microalgal community composition shift toward
increased diatom
dominance, and altered macrofaunal community
composition with lower
species richness, a larger proportion of insect
larvae, and a smaller
proportion of annelids, crustaceans, and
oligochaetes compared to
shaded (plant removal, shade mimic) and control
treatment plots.
Overall, the shaded treatment plots were similar
to the controls. Plant
cover removal also resulted in parallel shifts in
microalgal and
macrofaunal isotopic signatures of the most
dynamic species. This
suggests that animal responses are seen mainly
among microalgae grazers
and may be mediated by plant modification of
microalgae. Results of
these experiments demonstrate how light reduction
by the vascular plant
canopy can control salt marsh sediment communities
in an arid climate.
This research facilitates understanding of
sequential consequences of
changing salt marsh plant cover associated with
climate or sea level
change, habitat degradation, marsh restoration, or
plant invasion. 
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| Whitcraft,
C.
R.,
D. Talley, J. Crooks, J. Boland, and J. Gaskin.
2007. Invasion
of tamarisk (Tamarix spp.) in a southern
California salt
marsh. Biological Invasions 9(7): 875-879. |
|
Exotic plants have been demonstrated to be one of
the
greatest threats to wetlands, as they are capable
of altering
ecosystem-wide physical and biological
properties. One of the
most problematic invaders in the western United
States has been salt
cedar, Tamarix spp., and the impacts of this
species in riparian and
desert ecosystems have been well-documented. Here
we document large
populations of tamarisk in the intertidal salt
marshes of Tijuana River
National Estuarine Research Reserve, a habitat not
often considered
vulnerable to invasion by tamarisk. Initial
research demonstrates
that there are multiple species and hybrids of
Tamarix invading the
estuary and that the potential impact of tamarisk
within this salt
marsh is significant. This highlights the
need for managers and
scientists to be aware of the problems associated
with tamarisk
invasion of coastal marine habitats and to take
early and aggressive
action to combat any incipient invasion. 
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| Woulds, C., G. Cowie, L. Levin,
H. Andersson, J. Middelburg, S. Vandewiele, P.
Lamont, K. Larkin, A.
Gooday, S. Schumacher, C. Whitcraft, R.
Jeffreys, and M. Schwartz.
2007. The role of sea floor biological
communities in sedimentary
carbon cycling: oxygen and other controls. Limnology
and
Oceanography 52(4): 1698-1709. |
|
13C tracer experiments were conducted at sites
spanning
the steep oxygen, organic matter, and biological
community gradients
across the Arabian Sea oxygen minimum zone, in
order to quantify the
role that benthic fauna play in the short-term
processing of organic
matter (OM) and to determine how this varies among
different
environments. Metazoan macrofauna and
macrofauna-sized foraminiferans
took up as much as 56 6 13 mg of added C m22 (685
mg C m22 added) over
2–5 d, and at some sites this uptake was similar
in magnitude to
bacterial uptake and/or total respiration.
Bottom-water dissolved
oxygen concentrations exerted a strong control
over metazoan
macrofaunal OM processing. At oxygen
concentrations .7 mmol L21 (0.16
ml L21), metazoan macrofauna were able to take
advantage of abundant OM
and to dominate OM uptake, while OM processing at
O2 concentrations of
5.0 mmol L21 (0.11 ml L21) was dominated instead
by (macrofaunal)
foraminiferans. This led us to propose the
hypothesis that oxygen
controls the relative dominance of metazoan
macrofauna and foraminifera
in a threshold manner, with the threshold lying
between 5 and 7 mmol
L21 (0.11 to 0.16 ml L21). Large metazoan
macrofaunal biomass and
high natural concentrations of OM were also
associated with rapid
processing of fresh OM by the benthic community.
Where they were
present, the polychaete Linopherus sp. And the
calcareous foraminiferan
Uvigerina ex gr. semiornata, dominated the uptake
of OM above and
below, respectively, the proposed threshold
concentrations of
bottom-water oxygen. 
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