At present, there are nine LTER sites in
The MARAG project takes biodiversity and
productivity patterns along a rainfall gradient in
Along the rainfall gradient of The effect of woody vegetation on biodiversi=
ty and
ecosystem function is studied in the Israeli LTER sites situated along this
gradient. In each site we study how patch modification affects filtering of
species from the regional species to the patch assembly and its effects on =
the
system. The composition of woody vegetation alters from oak tree species in=
the
north to Hamada shrubs in the south, and percent plant cover also
changes. The woody vegetation pattern formation and filtering are expected =
to
be very different in the different sites. However, the sites are studied as=
a
network in order to identify patterns in biodiversity and productivity along
the rainfall gradient. The MARAG project was funded by the Israel S=
cience
Foundation, the Israel Nature & Parks Authority (INPA), the Israel Mini=
stry
of Science & Technology, Jewish National Fund (JNF) and the McDonnell
Foundation. Researchers from various institutions are involved in this
research. Participating institutions include The MARAG network is headed by Prof. Moshe S=
hachak
and a steering committee which includes Dr. Yehoshua Shkedy and Prof Avi
Perevolotzky. The central office of the MARAG is at the Blaustein Institute=
s of
Desert Research at BGU. Within the MARAG network the following taxa =
are
studied: plants, springtails, beetles, grasshoppers, spiders and
microorganisms. Each site has a site manager who oversees the plant research
(Avdat – Dr. Bert Boeken; Lehavim – Dr. Eugene Ungar; Adulam
– Dr. Yariv Malichi; Ramat Hanadiv – Prof. Avi Perevolotzky; Me=
ron
– Prof. Gidi Ne’eman), while the animal research is organized by
Prof. Yael Lubin (BGU) and Dr. Elli Groner (BGU). The microorganism researc=
h is
headed by Dr. Osnat Gillor (BGU). To ensure that the study is networked, at ea=
ch site
species diversity of the chosen taxa is sampled using the same protocol in =
both
woody and open (non-woody) patches. In addition the same experimental desig=
n is
used in all sites. Woody vegetation was previously removed to enable us to
study patch characteristics with and without woody vegetation. Since grazin=
g is
practiced in most of Israel, its effect on species diversity was included in
the monitoring. In half of the plots at each site grazing is excluded while=
in
the other half grazing is introduced. Overall there are four treatments
assigned to each site (see Table 1): grazing-shrub removal (RG), no
grazing-shrub removal (RX), no grazing-no shrub removal (UX), grazing-no sh=
rub
removal (UG). Table 1: Classification of terms used for th=
e four
experimental treatments used in the MARAG study. Woody vegetation removal (R) Unremoved (U) Grazing (G) RG UG Grazing excluded (X) RX UX The MARAG project also emphasizes theoretical
studies by developing conceptual and mathematical models. Profs Ehud Meron =
and
Moshe Shachak (BGU) developed models to explain the relationships among
vegetation pattern formation, ecosystem function, species filtering and bio=
mass
production. The MARAG network is testing the models using field data relate=
d to
vegetation patterns and their effect on biodiversity. Dr. Yochai Carmel
(Technion) is testing the vegetation patterns–diversity relationship
using aerial photographs All of the data is managed by Prof. Ronen Kadmon
(HUJI) and is available for synthesis to reveal general patterns of biodiversity c=
hanges
along the rainfall gradient. The results are used to design ecosystem
management models. The management part of the project is headed by Dr. Yeho=
shua
Shkedi (INPA), Prof. Avi Perevolotsky (ARO) and Dr. Eugene Ungar (ARO). This project is about to expand to include
management supporting research, environmental education research and additi=
onal
LTER sites. Below are details of the sites that are either part of the proj=
ect
or are being considered for inclusion in the network. Table of Site
Characteristics Avdat, Central Negev, Israel, annual rainfall: 90 mm Head of LTER site: Dr. Bertrand Boeken The Wyler Department of Dryland Agriculture, The Jacob Blaustein Institutes for Desert Research, Ben-Gurion University of the Negev, Sede Boqer Campus, Israel 84990 Email: bboeken@bgu.=
ac.il
Latitude 30° 47' N; longitude 34° 46' E; elevati=
on
600-700 m; size 700 ha. Arid shrub-steppes consisting of rock=
y slopes
and loessial ephemeral streambed=
s and
ancient agricultural terraces. Mean maximum summer temperature is 32 ºC; mean minimum winter temperature is 5
ºC. Vegetation is dominated by dwarf shrubs (=
Hamada
scoparia on plains, Artem=
isia
crassifolia and Zygophyllum dumosum on slopes). Ancient surface runoff agriculture; hydrolog=
y of
runoff; dryland agroforestry; population and community ecology of herbaceous
plants and invertebrates; biodiversity and ecosystem management; ecosystem
engineering and patch dynamics; food-web dynamics; watershed modeling; soil
fauna dynamics. The site was established in 1958 by the Hebr=
ew
University of Jerusalem. Livestock grazing has taken place in the area for
thousands of years. Remains of ancient Nabatean runoff agriculture (ca. 0-3=
00
AD) in the form of terraces are still evident. Currently Bedouin inhabitants
practice sedentary pastoralism with goats, sheep and camels. Livestock graz=
ing
has been excluded from parts of the site. Meteorological monitoring (a=
ir
and soil temp, RH, wind velocity, rainfall and soil moisture); runoff
production and harvesting; sedimentation and erosion; shrub demography;
arthropod and annual plant population density and community structure in
relation to livestock grazing and shrub cutting; vertebrate and invertebrate
predator/prey dynamics; soil fauna distribution and dynamics. Lehavim, Northern Negev, Israel, annual rainfall: 200 mm Latitude 31° 25' N; longitude 34° 48' E; elevati=
on
300-400 m; size 800 ha. Head of LTER site: Dr Eugene Ungar Department of Natural Resources, Agricultural Research Organization-Volcani Center, POB 6, Bet Dagan, 50250, Israel Email: eugene@volcani.agri.gov.il Semi-arid desert; shrub and grass steppes, r=
ocky and
loessial watersheds, dry riverbeds, rangeland. Animals and ecosystem functions; biodiversit=
y and
ecosystem functions; desertification; disturbances; ecosystem management;
effects of grazing; landscape dynamics; nutrient cycling; plant community
dynamics; primary production dynamics; remote sensing; spatial and temporal
distribution of grazing; watershed hydrology, geomorphology and ecology. The
Lehavim site is a range management research station in the northern Negev,
14 km north of Beer Sheva. Before the establishment of the site in 1980
the area had been under grazing pressure for thousands of years. Since 1980=
the
area has been managed by the Ministry of Agriculture and the Jewish National
Fund (JNF). In 1980, communal grazing by Bedouin sheep herds on the site was
replaced by controlled grazing under moderate stocking rates. This was done=
by
fencing the entire area and allowing only two herders to use the area
exclusively. Since 1980 the site has served as a site for demonstrating
appropriate range and livestock management. In 1992 a network of fifty (10 =
x 10
m) exclosures was established on the predominant habitats of the site, enab=
ling
monitoring of grazing impact and removal. In 1997 the area was declared par=
t of
the DEN (Dryland Ecosystem-management Network). The types of data collected
include: changes in landscape mosaic; density, biomass and species diversit=
y of
annual plants in grazed and ungrazed areas; effects of different stocking r=
ates
on plant communities; soil fertilization; herd movements; organic matter and
soil flows by surface runoff across the landscape; primary production dynam=
ics;
rainfall and soil moisture dynamics; runoff water generation and erosion; s=
eed
bank dynamics; spectral reflectance; and variations in annual plant species
composition due to grazing. A meterological station operates at the site un=
der
the supervision of Dr. Eli Zaadi (ARO) (http://www.c=
mc-amman.gov.jo/mems/CMC/Public/index.php).
More information on the site can be found at Sayeret Shaked Park, northern Negev, Israel, annual rainfall: 300 mm Principal contact and institution Dr. Bertrand Boeken The Wyler Department of Dryland Agriculture, The Jacob B=
laustein
Institutes for Desert Research, Ben-Gurion University of the Negev, Sede Bo=
qer
Campus, 84990 Israel Email: bboek=
en@bgu.ac.il Latitude 31° 17' N; longitude 34° 37' E; elevation
200 m; size 300 ha. Semi-arid shrubland (shrub-grass steppe), ro=
cky and
loessial watersheds, ephemeral streams, loessial plains. Vegetation
is dominated by dwarf shrubs (Noaea mucronata, Atractylis serratuloides =
and Thymelea hirsuta). M=
ean
maximum summer temperature is 34 ºC, mean minimum winter temperat=
ure
6 ºC. Vegetation, resource and landscape dynamics;
biodiversity and ecosystem function; desertification; disturbances; ecosyst=
em
management; livestock grazing; nutrient cycling; organic matter dynamics;
ecosystem engineering; remote sensing; watershed modeling. The Sayeret Shaked site is an ecological par=
k in the
northern Negev near the town of Ofakim. Before the establishment of the par=
k in
1987 the area had been under grazing pressure for thousands of years. Since
1987 the area has been managed by the JNF. Management includes livestock
grazing, landscape alterations, runoff water harvesting and tree planting.
Approximately 30 ha of the park is fenced to exclude livestock grazing and =
is
designated for research. From 1994 the area has been a demonstration site f=
or
the International Arid Lands Consortium. Since 1997 the area has been part =
of
DEN (Dryland Ecosystem-management Network, the Israeli LTER network). Meteorological monitoring (air and soil temp=
, RH,
wind velocity, rainfall and soil moisture – see http://www.middleeast.sandia.gov/);
changes in landscape mosaics; density, biomass and species diversity and
population dynamics of annual plants in natural, grazed, disturbed and mana=
ged
areas; shrub demography; dust and organic matter deposition; litter deposit=
ion;
nitrogen flux; movement of organic matter by surface runoff; recovery of cr=
ust
and shrub patches; runoff water generation and erosion from disturbed and
undisturbed areas; seed bank dynamics; snail, ant and termite population
dynamics; spectral reflectance. Nizzanim, southern Mediterranean coast, Israel, annual rainfall: =
400
mm Head
of LTER site: Prof. Haim Tsoa=
r -
Geomorphology and Prof.
Pua Bar (Kutiel) – Ecology, Department
of Geography and Environmental Development, Beer-Sheva
84105,
Israel Email:
tsoar@bgu.ac.il; kutiel@bgu.ac.il Sand dunes (mobile, semi-stabilized and stab=
ilized)
within a Mediterranean climate (450-500 mm of rain per year). Shrubland
dominated by Saharo-Arabian shrubs (Artemisia monosperma and Reta=
ma
Retama) accompanied by Mediterranean herbaceous species, some of which =
are
endemic. =
Coastal dune geomorphology and ecology dynam=
ics and
their interactions; effect of change in land-use on dune morphology and
dynamics; landscape changes; vegetation, animals (small mammals, reptiles, =
arthropods) and ecosystem functions; biodivers=
ity;
disturbances; ecosystem conservation, restoration and management; effect of
vegetation removal (uprooting and grazing) on re-establishment of sand-lovi=
ng
species and sand mobility; bioindicator species; landscape dynamics; plant<=
span
style=3D'mso-spacerun:yes'> and animal community dynamics; GIS=
and
remote sensing; habitat definition and characterization (patterns); patchin=
ess;
scales. &=
yacute; Titles
of studies currently being conducted at Nizzanim sand dune site: ý
Sustainable management of coastal dunes for
biodiversity conservation. ý
Conserving sand dunes and dune life: regional
scientific inputs for effective management policies. ý
The spread rate of the invasive plant Aca=
cia
saligna at ý
Ecology and biology of A. saligna seed
bank under natural and managed conditions. ý
The phenotypic/genotypic plasticity of the
invasive plant Heteroteca subexillaris and its impact on sand dune
ecosystems. ý
The water regime at Nizzanim sand dunes as
affected by biotic and abiotic processes. =
The sand dunes of Nizzanim were subjected to=
human
interference (firewood cutting, grazing, and plantations) for several decad=
es
in the second half of the 20th century. Since then the area has =
been
protected on various levels, which has accelerated dune stabilization due to
shrub encroachment. As a consequence, characteristic geomorphic features and
plant and animal communities have changed. In 2006, 1900 out of 3000 ha of =
sand
dunes were declared as a nature reserve. The area is under the auspices of =
the
JNF (Jewish National Fund), INPA (Israel Nature & Parks Authority) and =
The
SPNI (Society for the Protection of Nature in Changes in dune dynamics and
morphology; tracing the effect of vegetation removal since 2001; sand erosi=
on
and deposition; vegetation (cover, abundance biomass, composition) and anim=
als
(abundance and composition) on the dune scale (mobile, semi-stabilized and
stabilized dunes) and the patch scale (open and under shrubs). The data are
simultaneously collected from both non-manipulated and manipulated dunes (f=
rom
which the vegetation was removed to various levels of coverage in April 200=
5).
Altogether there are 23 dunes under observation, and 3-4 monitoring expedit=
ions
per year. =
Adulam<=
b>, Latitude 31&de=
g; 38'
N; longitude 34° 56' E; elevation 400 m. Head of LTER site: Dr Yariv Malihi District ecologist, Israel Nature & Parks Authority
(INPA) Email: yariv.m@npa.org.il Dry Mediterranean climate - average annual r=
ainfall
400 mm with 20.5 °C average temperature. Low trees, mainly Quercus Calliprinos and Pistacia Palaes=
tina
with dense shrubs of Phillyrea latifolia and Pistacia
lentiscus on Eocene limestone=
. Ecosystem functions; biodiversity; ecosystem
management; effect of grazing and plant removal on species diversity; plant
community dynamics; primary production dynamics. The Adulam site is situated in the western p=
art of
the Judean Hills, 30 km southwest of Jerusalem. Before the declaration of
Adulam as a nature reserve in 1994, the area had been under grazing pressure
for thousands of years. Since 1994 the area has been managed by the INPA and
communal grazing by Bedouin sheep herds on the site was replaced by control=
led
grazing under moderate rates. The research site became a part of the Israeli
LTER project in 2003. The research scheme is 12 plots of 45x45 met=
ers, six
on a northern slope and six on a southern slope. The treatments include: pl=
ant
removal, grazing, and a combination of grazing and plant removal and contro=
l. Data collected include: tree
re-growth rate; reptile, snail and rodent diversity and community compositi=
on;
density, biomass and species diversity of annual plants in grazed and
non-grazed areas; variations in annual plant species composition due to
grazing. Ramat Hanadiv, Southern Mt. Carmel, Israel, Annu=
al
rainfall: 600 mm Latitude 32° 33' N; longitude 34° 56' E; elevati=
on
120 m (max); size 500 ha. Head of LTER site:
Prof. Avi Perevolotsky, Department of Natural Resources, Agricultural Research Organization-Volcani Center, POB 6, Bet Dagan 50250, Israel Email: avi@agri.gov.il Research director: Liat Hadar, Ramat Hanadiv Nature Park, P.O.B 325, Zichron Ya'acov 30900, Israel Email: Mediterranean garrigue, Mediterranean maquis=
, open
rangelands, planted pine and cypress groves, rocky cliffs, dry riverbeds,
spring, orchard, cultivated garden. Ecosystem management; effect of cattle and g=
oat
grazing; effect of shrub clearing and thinning; shrub encroachment;
biodiversity and population dynamics of selected animal groups as
bio-indicators: songbirds, butterflies, chukars, gazelles, snails; biodiver=
sity
of herbaceous plant community; biodiversity and management; landscape dynam=
ics;
historical mapping of woody vegetation; management for rare species; manage=
ment
for multi-purpose use; pine colonization. The Ramat Hanadiv LTER site is located in the Southern part of Mt. C=
armel,
in the Mediterranean region of Israel. The park covers an area of 500 hecta=
res,
and is patchy in nature and rich in biological diversity. The
area is covered by garrigue communities, dominated by the moderate-sized sh=
rubs
Phillyrea media, Pistacia lentiscus, Calycotome villosa and the dwarf s=
hrub
Sarcopoterium spinosum. It has experienced a long history of human u=
sage
and impact, including grazing and clearing activities. The park was fenced =
in
1950 and grazing was excluded for 40 years. The area was burnt by a wild-fi=
re
in 1980. In 1992, a fuel break zone was established in the park to reduce f=
ire
damage and distribution. Technically
the private property of the Rothschild family, the area was designated by t=
he
Rothschild Foundation twenty years ago for public use, education and ecolog=
ical
research. However, during these twenty years, mostly short-term scientific
research, both applied and pure, has been carried out in the park. Today, t=
he
orientation is towards long-term thinking and planning, including an LTER s=
ite
established in 2003. The
types of data collected (on a routine basis) include: herbaceous community
diversity and woody vegetation structure, in different habitats and grazing
regimes; population dynamics and habitat preferences of gazelles, wild boar=
s,
jackals, mongoose and chukars; species diversity and habitat preferences of
butterflies, songbirds and snails; monitoring re-introduced raptors and roe
deer. The
park is a distinctive example in Israel of a well-investigated and
carefully-managed natural area. As such, it has become a model for the
conservation, rehabilitation and management of Mediterranean ecosystems in
Israel. More
information can be found at: http://www.ramat-hana=
div.co.il/index_en.aspx
Jerusalem, Kislon wadi, Kdoshim forest,
Israel, annual rainfall: 700 mm Latitude N, longitude
E, elevation m; size ha. Hanoch Tzoref (JNF) Man-made pine forest. Biodiversity conservation; primary productiv=
ity;
regrowth; ecosystem services; forest management; modeling. This forest is about 45 years old. It has a =
history
of fires, snowfalls, tree cutting and natural regrowth of native Mediterran=
ean
flora.
1. Site name and location
Principal contact and institution
Location
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Data collected
2. Site name and location
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3. Site name and location
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4. Site name and location
Latitude 31o 44'22"N; longitude:34o 36'30"E;
elevation 0-50 m; size 1900 ha.Principal contact and institution
Principal biome/main communities
Research topics
History of site
Data collected
5. Site name and location
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6. Site name and location
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7. Site name and location
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