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      <P align=3Dcenter><A class=3Dnav=20
      =
href=3D"http://www.brown.edu/Departments/EEB/bertness/index.htm">Biograph=
y</A>&nbsp;|&nbsp;<SPAN=20
      class=3Dnav>Research</SPAN>&nbsp;|&nbsp;<A class=3Dnav=20
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    <TD class=3Dtext vAlign=3Dtop width=3D310>
      <DIV align=3Dright>Robert P. Brown Professor of Biology<BR>(401)=20
      863-2280<BR><A class=3Dnav=20
      =
href=3D"mailto:Mark_Bertness@brown.edu">Mark_Bertness@brown.edu</A>=20
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          <TD class=3Dtext vAlign=3Dtop>
            <P><IMG height=3D202 alt=3DWave hspace=3D4=20
            =
src=3D"http://www.brown.edu/Departments/EEB/bertness/wavefoam.jpg"=20
            width=3D304 align=3Dright border=3D1> I am interested in the =
biological=20
            and physical processes that generate pattern in natural =
communities=20
            and the role that experimental community ecology can play in =

            improving the conservation and management of natural and =
human=20
            impacted ecosystems. I usually work in shoreline =
communities, since=20
            they are particularly good model systems to elucidate how =
biotic and=20
            physical factors interact to organize and structure natural=20
            communities. Much of my work is focused on salt marshes not =
just=20
            because they are good model systems, but because they are=20
            ecologically and economically important and in many parts of =
the=20
            world are seriously threatened by human population pressure. =
</P>
            <P class=3DheadRed>SALT MARSH PLANT COMMUNITIES</P>
            <TABLE cellSpacing=3D0 cellPadding=3D4 align=3Dleft =
border=3D0>
              <TBODY>
              <TR>
                <TD class=3Dunderpic><IMG height=3D148 alt=3D"Maine =
marshes"=20
                  hspace=3D4=20
                  =
src=3D"http://www.brown.edu/Departments/EEB/images/bertness2.jpg"=20
                  width=3D223 align=3Dtop vspace=3D4 border=3D1><BR><A=20
                  =
href=3D"http://www.brown.edu/Departments/EEB/bertness/mm.htm">Click=20
                  to enlarge image</A></TD></TR></TBODY></TABLE>For over =
two decades=20
            my students and I have explored processes that generate =
spatial=20
            patterns in New England salt marsh plant communities. Our =
work on=20
            these ecologically critical habitats has examined the =
relative=20
            importance of plant competition, plant-animal interactions, =
physical=20
            disturbance and positive feedbacks in generating and =
maintaining the=20
            often-striking patterns in these systems. The relative =
simplicity of=20
            these systems makes them ideal for experimental manipulation =
and=20
            addressing questions about the general organization of =
communities.=20
            We have found that in New England while plant competition is =
largely=20
            responsible for the distribution patterns of plants across =
marsh=20
            landscapes, positive interactions among marsh plants are =
often=20
            responsible for making the physically harsh marsh habitat=20
            inhabitable. For example, in low marsh habitats, oxygen =
depleted,=20
            anoxic substrate can limit the success of plants. In these =
habitats,=20
            however, groups of plants can colonize and communally =
oxygenate=20
            anoxic substrate by supplying their roots with oxygen =
leading to=20
            high plant production. Analogously, at higher marsh =
elevations plant=20
            success can be limited by high soil salinities that are the =
result=20
            of evaporation of pore water in marsh sediments. In these =
habitats=20
            colonization by salt tolerant plants shade the soil, lower =
soil=20
            salinities and facilitate the invasion and success of plants =
that=20
            are not as salt tolerant. Much of my ongoing work with salt =
marshes=20
            is exploring the how common these types of positive =
feedbacks are in=20
            natural assemblages and examining the implications of these =
findings=20
            on our current understanding and conservation of shoreline=20
            communities.
            <P></P>
            <P class=3DheadRed>HUMAN IMPACTS ON SALT MARSH PLANT =
COMMUNITIES</P>
            <TABLE height=3D163 cellSpacing=3D0 cellPadding=3D4 =
align=3Dright=20
              border=3D0><TBODY>
              <TR>
                <TD class=3Dunderpic height=3D163><IMG height=3D163=20
                  alt=3D"Southern New England marshes"=20
                  =
src=3D"http://www.brown.edu/Departments/EEB/images/bertness4.jpg"=20
                  width=3D251 align=3Dtop border=3D1><BR><A=20
                  =
href=3D"http://www.brown.edu/Departments/EEB/bertness/snem.htm">Click=20
                  to enlarge image</A></TD></TR></TBODY></TABLE>
            <P><B>Southern New England marshes</B>=20
            <P>Our work with nutrient limitation in Southern New England =
salt=20
            marshes has revealed that the traditional plant zonation of =
New=20
            England salt marshes described early in the 20th century was =
largely=20
            driven by competition for nitrogen. Contemporary New England =

            landscapes are being taken over by cordgrass (Spartina =
alterniflora)=20
            and invasive Phragmites australis due to shoreline =
development and=20
            eutrophication. Shoreline development removes vegetative =
buffers=20
            from marshes, triggering increased nitrogen input. This =
relaxes=20
            competition for nitrogen and consequently, cordgrass and =
Phragmites,=20
            dominant light competitors, competitively exclude all other =
plants=20
            reducing plant diversity dramatically and leading to a =
simplified=20
            landscape dominated by stands of these two plants. Thus our =
work in=20
            New England has lead to a simple mechanistic understanding =
of how=20
            humans are triggering extensive species composition shifts =
in these=20
            communities and suggests how these communities can be =
managed to=20
            minimize human impacts. We are currently exploring the =
generality of=20
            these results in other systems and exploring the links =
between=20
            eutrophication and consumer control in New England and South =

            American marshes. <BR></P>
            <P class=3DheadRed>CLIMATE-DRIVEN PATTERNS IN THE =
ORGANIZATION OF SALT=20
            MARSH PLANT COMMUNITIES</P>
            <P><IMG height=3D192 alt=3DGreenhouses hspace=3D4=20
            =
src=3D"http://www.brown.edu/Departments/EEB/bertness/greenhouses.jpg"=20
            width=3D365 align=3Dleft border=3D1></P>The role of climate =
in influencing=20
            the structure and organization of marsh plant communities is =
not=20
            well understood, but important if we are going to be able to =
predict=20
            how global warming over the next century will impact salt =
marshes=20
            and the ecological and societal services that they provide. =
We are=20
            currently exploring the potential role of climate in =
influencing=20
            marsh plant zonation patterns by affecting physical =
gradients across=20
            salt marsh landscapes. In particular, we are examining the=20
            hypothesis that by controlling evaporative processes and the =

            potential accumulation of salt in marsh soils, climate may =
determine=20
            the importance of soil salinity in influencing the =
distribution and=20
            abundance of plants across marsh habitats and overall marsh =
primary=20
            production. A powerful approach to exploring the linkage =
between=20
            climate and the organization of communities is to examine =
natural=20
            latitudinal variation in community structure. Along the east =
coast=20
            of North America salt marsh plant communities are a common =
shoreline=20
            habitat from the Canadian Maritime provinces to central =
Florida,=20
            where marshes give way to mangrove forests, the tropical =
analog to=20
            salt marshes. Whereas marshes North of central Maine differ =
from=20
            more Southerly marshes due to the heavy, chronic impact of =
winter=20
            ice, marshes from Southern Maine to Florida are composed of =
a=20
            similar suite of plants. We are using these marshes as a =
model=20
            system to examine the effects of climate on plant community=20
            organization. We are using experimental greenhouses to test =
the=20
            hypothesis that climatic warming will increase the =
productivity of=20
            Northern marshes, but decrease the productivity of Southern =
marshes=20
            by increasing the size and geographic extent of low =
productivity=20
            salt pans. The role of climate in influencing the structure =
and=20
            organization of marsh plant communities is largely =
unexplored, but=20
            an important topic if we are going to be able to predict how =
global=20
            warming over the next century will impact salt marshes and =
the=20
            ecological and societal services that they provide. We are =
currently=20
            exploring the potential role of climate in influencing marsh =
plant=20
            zonation patterns by affecting physical gradients across =
salt marsh=20
            landscapes. In particular, we are examining the hypothesis =
that by=20
            controlling evaporative processes and the potential =
accumulation of=20
            salt in marsh soils, climate may determine the importance of =
soil=20
            salinity in influencing the distribution and abundance of =
plants=20
            across marsh habitats and overall marsh primary production.
            <P></P>
            <P>A powerful approach to exploring the linkage between =
climate and=20
            the organization of communities is to examine natural =
latitudinal=20
            variation in community structure. Along the east coast of =
North=20
            America salt marsh plant communities are a common shoreline =
habitat=20
            from the Canadian Maritime provinces to central Florida, =
where=20
            marshes give way to mangrove forests, the tropical analog to =
salt=20
            marshes. Whereas marshes North of central Maine differ from =
more=20
            Southerly marshes due to the heavy, chronic impact of winter =
ice,=20
            marshes from Southern Maine to Florida are composed of a =
similar=20
            suite of plants. We are using these marshes as a model =
system to=20
            examine the effects of climate on plant community =
organization. We=20
            are doing this by using greenhouses at salt marsh that =
increase air=20
            temperature by ~3oC at study sites in Maine, Rhode Island, =
Georgia=20
            and Florida. We are testing the explicit hypothesis that =
climatic=20
            warming will increase the productivity of Northern marshes, =
but=20
            decrease the productivity of Southern marshes by increasing =
the size=20
            and geographic extent of low productivity salt pans. </P>
            <TABLE cellSpacing=3D0 cellPadding=3D4 align=3Dleft =
border=3D0>
              <TBODY>
              <TR>
                <TD class=3Dunderpic><IMG height=3D169 alt=3D"Georgia =
marshes"=20
                  =
src=3D"http://www.brown.edu/Departments/EEB/images/bertness1.jpg"=20
                  width=3D259 align=3Dtop border=3D1><BR><A=20
                  =
href=3D"http://www.brown.edu/Departments/EEB/bertness/gm.htm">Click=20
                  to enlarge image</A></TD></TR></TBODY></TABLE>
            <P class=3DheadRed>CONSUMER CONTROL OF MARSH PLANT =
PRODUCTION</P>Salt=20
            marsh ecosystems are widely considered to be controlled =
exclusively=20
            by bottom up forces, but there is mounting evidence that =
human=20
            disturbances are triggering consumer control in western =
Atlantic=20
            salt marshes, often with catastrophic consequences. The =
entrenched=20
            view that salt marshes are controlled largely by bottom-up =
forces=20
            was seriously challenged when, my former graduate student =
and=20
            current collaborator, Brian Silliman found that the snail =
Littoraria=20
            irrorata could potentially exert strong top-down, consumer =
control=20
            over marsh production. Since that time we have examined and =
found=20
            strong evidence for consumer control triggered by human =
disturbance=20
            on the Southeastern and Gulf coasts of the US by snails, on =
the=20
            Atlantic and Pacific coasts of South America by crabs and =
cattle=20
            gazing, respectively, and in New England by insects and a =
nocturnal,=20
            native crab. In many of these systems, once consumer control =
is=20
            triggered it is leading to run away consumption, salt marsh =
die offs=20
            and the loss of salt marshes and the services they provide.=20
            Together, these examples warn that while historically salt =
marshes=20
            may have been under bottom up control, human disturbances =
ranging=20
            from the use of nitrogen fertilizers, over-harvesting top =
predators,=20
            climate-change induced drought and exotic consumer invasions =
are=20
            stimulating consumer control in salt marsh ecosystems, =
sometimes=20
            with catastrophic results. Understanding the emerging role =
of=20
            consumers in human disturbed marshes, particularly as they =
relate to=20
            salt marsh die off phenomena, is a major current focus of my =
lab.=20
            <P class=3DheadRed>ROCKY INTERTIDAL COMMUNITIES</P>
            <TABLE height=3D163 cellSpacing=3D0 cellPadding=3D4 =
align=3Dright=20
              border=3D0><TBODY>
              <TR>
                <TD class=3Dunderpic height=3D163><IMG height=3D141=20
                  alt=3D"Maine Rocky Shores"=20
                  =
src=3D"http://www.brown.edu/Departments/EEB/images/bertness3.jpg"=20
                  width=3D219 align=3Dtop border=3D1><BR><A=20
                  =
href=3D"http://www.brown.edu/Departments/EEB/bertness/mrs.htm">Click=20
                  to enlarge image</A></TD></TR></TBODY></TABLE>
            <P><B>Maine Rocky Shores</B></P>
            <P>I am also interested in rocky intertidal communities and =
have a=20
            research program at the Darling Center of the University of =
Maine=20
            using Gulf of Maine rocky shores to explore community =
organization=20
            questions. In the past few years we have examined the =
biogeography=20
            of thermal stress ameliorating group benefits in barnacles =
and=20
            seaweeds, the role of flow in influencing marine benthic =
communities=20
            and the importance of predator (crab) cues in influencing =
consumer=20
            (snail) behavior and indirectly benthic community structure. =
We have=20
            also recently tested the idea that intertidal communities =
can=20
            represent alternate stable states on rocky shores in the =
Gulf of=20
            Maine. It has been suggested that intertidal mussel beds and =
seaweed=20
            canopies represent alternate community stable states on =
rocky shores=20
            in the Gulf of Maine. This theoretically appealing idea =
hypothesizes=20
            that these habitats are disturbance patch mosaics that can =
be=20
            dominated by either seaweed canopies or mussel beds, and =
that which=20
            community occurs in a given habitat is stochastic and =
dependent on=20
            the size of the original disturbance and recruit =
availability. Large=20
            disturbances are postulated to be dominated by mussel beds =
and=20
            barnacles that have widely dispersed larvae, while smaller=20
            disturbances are dominated by seaweeds, which have limited=20
            dispersal. Positive feedbacks are proposed to maintain the =
stability=20
            of these two distinct communities. We have experimentally =
exploring=20
            this idea and to date have found that in general mussel beds =
and=20
            seaweed canopies are highly deterministic states dictated by =
flow=20
            patterns and consumer pressure. We are currently trying to =
rectify=20
            these results with the alternate stable state =
hypothesis.</P>
            <P class=3DheadRed>SOUTH AMERICAN SHORELINE ECOLOGY</P>
            <TABLE cellSpacing=3D0 cellPadding=3D4 width=3D200 =
align=3Dleft border=3D0>
              <TBODY>
              <TR>
                <TD class=3Dunderpic><IMG height=3D199=20
                  alt=3D"Patagonian Rocky Shores"=20
                  =
src=3D"http://www.brown.edu/Departments/EEB/images/Patagonian_rocky_shore=
s.jpg"=20
                  width=3D266 align=3Dtop border=3D1><BR><A=20
                  =
href=3D"http://www.brown.edu/Departments/EEB/bertness/prs.htm">Click=20
                  to enlarge image</A></TD></TR></TBODY></TABLE>
            <P>I am generally interested in the comparative ecology of =
South and=20
            North American shoreline communities. My students and I are =
working=20
            in Argentina with rocky intertidal shores in central =
Patagonia and=20
            with salt marshes in northern Argentina, southern Brazil =
central=20
            Chile. The goal of this work is to test the robustness of =
our North=20
            American-biased understanding of these systems on their much =
less=20
            studied South American counterparts, develop collaborations =
with=20
            South American faculty and graduate students and build =
scientific=20
            capacity in marine ecology and conservation biology in Latin =

            America.</P>
            <TABLE cellSpacing=3D0 cellPadding=3D4 align=3Dright =
border=3D0>
              <TBODY>
              <TR>
                <TD class=3Dunderpic><IMG height=3D187 alt=3D"Patagonian =
Shores"=20
                  =
src=3D"http://www.brown.edu/Departments/EEB/images/Pategonian_shores.jpg"=
=20
                  width=3D250 align=3Dtop border=3D1><BR><A=20
                  =
href=3D"http://www.brown.edu/Departments/EEB/bertness/ps.htm">Click=20
                  to enlarge image</A></TD></TR></TBODY></TABLE>
            <P><B>Patagonian Rocky Shores</B></P>
            <P>On rocky shores in Patagonia we are experimentally =
examining the=20
            roles of consumers, desiccation stress and wave exposure in=20
            generating the structure of South American intertidal =
assemblages.=20
            We have done similar studies in Maine intertidal systems for =

            comparison. On Patagonian rocky shores we are also examining =

            ecosystem engineering and the community structuring role of =
mussel=20
            beds on wave exposed headlands on Patagonian rocky shores =
which=20
            appear to facilitate the success of virtually all the other=20
            intertidal benthic organisms that live in this particularly=20
            physically stressful habitat.</P>
            <P><B>South American Salt Marshes</B></P>
            <TABLE cellSpacing=3D0 cellPadding=3D4 align=3Dleft =
border=3D0>
              <TBODY>
              <TR>
                <TD class=3Dunderpic><IMG height=3D199 alt=3D"Home in =
Patagonia"=20
                  =
src=3D"http://www.brown.edu/Departments/EEB/images/Home_in_Patagonia.jpg"=
=20
                  width=3D266 align=3Dtop border=3D1><BR><A=20
                  =
href=3D"http://www.brown.edu/Departments/EEB/bertness/hip.htm">Click=20
                  to enlarge image</A></TD></TR></TBODY></TABLE>
            <P>We are exploring the role of consumers in South American =
salt=20
            marsh systems to compliment our work in North American salt =
marshes=20
            that has demonstrated strong consumer control of marsh =
production.=20
            In Argentinean marshes we are examining the hypothesis that =
the=20
            exceedingly abundant crab, Chasmagnathus granulata, exerts =
strong=20
            top-down control on plant production in these poorly studied =

            systems. On the Chilean coast we are examining the =
interactive roles=20
            of nutrient limitation and cattle grazing in controlling =
salt marsh=20
            plant production and distribution and abundance =
patterns.</P>
            <P>To facilitate our work in South America we have =
collaborative=20
            relationships with the laboratories of Lobo Orensanz at the =
CONICET:=20
            Argentine Council for Science, Puerto Madryn, Oscar Irbarne =
at the=20
            University of Mar del Plata in Argentina, Cesar Costa at the =

            National University of Rio Grande in Brazil and Kongo Farina =
at the=20
            Catholic University of Santiago, Chile. We are co-advising =
and=20
            collaborating with South American graduate students in each =
of these=20
            labs.</P>
            <P><A=20
            =
href=3D"http://www.brown.edu/Departments/EEB/bertness/research.htm#top">t=
op</A>=20
            </P></TD></TR></TBODY></TABLE><!-- InstanceEndEditable -->
      <P>&nbsp;</P></TD>
    <TD vAlign=3Dtop rowSpan=3D4><IMG height=3D548 alt=3D""=20
      =
src=3D"http://www.brown.edu/Departments/EEB/images/interior_r5_c4.gif"=20
      width=3D20 border=3D0 name=3Dinterior_r5_c4></TD>
    <TD height=3D34></TD></TR>
  <TR><!-- InstanceBeginEditable name=3D"body" --><!-- =
InstanceEndEditable -->
    <TD height=3D191><IMG height=3D191 alt=3D""=20
      src=3D"http://www.brown.edu/Departments/EEB/images/spacer.gif" =
width=3D1=20
      border=3D0></TD>
    <TD></TD></TR>
  <TR>
    <TD rowSpan=3D2><IMG height=3D357 alt=3D""=20
      src=3D"http://www.brown.edu/Departments/EEB/images/spacer.gif" =
width=3D1=20
      border=3D0></TD>
    <TD height=3D186></TD></TR>
  <TR>
    <TD vAlign=3Dtop colSpan=3D4 height=3D75>
      <P align=3Dcenter><FONT face=3D"Verdana, Arial, Helvetica, =
sans-serif"=20
      size=3D2>Box G, Brown University, Providence, RI 02912<BR>ph: =
401.863.3324 |=20
      e-mail: <A=20
      =
href=3D"mailto:Carol_Casper@brown.edu">Carol_Casper@brown.edu</A></FONT><=
/P>
      <P align=3Dcenter><FONT face=3D"Verdana, Arial, Helvetica, =
sans-serif"=20
      size=3D1>Copyright =A9 2003 Brown University. All Rights Reserved. =
<BR>Site=20
      design <A href=3D"http://www.academicwebpages.com/">Academic Web=20
      Pages</A></FONT></P></TD>
    <TD></TD></TR>
  <TR>
    <TD height=3D1></TD>
    <TD></TD>
    <TD width=3D262></TD>
    <TD></TD>
    <TD></TD>
    <TD></TD>
    <TD></TD>
    <TD></TD></TR></TBODY></TABLE><!-- InstanceEnd --></BODY></HTML>

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	LIST-STYLE-IMAGE: none; TEXT-INDENT: 30px; FONT-FAMILY: Arial, =
Helvetica, sans-serif; LIST-STYLE-TYPE: none
}
.booktitle {
	FONT-WEIGHT: bold; FONT-SIZE: 16px; COLOR: #336699; FONT-FAMILY: Arial, =
Helvetica, sans-serif
}
A:hover {
	COLOR: #ff0000; FONT-FAMILY: Verdana, Arial, Helvetica, sans-serif
}
.nav {
	FONT-WEIGHT: bold; FONT-SIZE: 12px; COLOR: #000000; FONT-FAMILY: Arial, =
Helvetica, sans-serif
}
.headRed {
	FONT-WEIGHT: bold; FONT-SIZE: 14px; COLOR: #663333; FONT-FAMILY: =
Verdana, Arial, Helvetica, sans-serif
}
.underpic {
	FONT-SIZE: 10px; FONT-STYLE: italic; FONT-FAMILY: Arial, Helvetica, =
sans-serif; TEXT-ALIGN: center
}

------=_NextPart_000_004E_01CA386D.4A115100--

