Content uploaded by Mazin Qumsiyeh
Author content
All content in this area was uploaded by Mazin Qumsiyeh on Aug 14, 2021
Content may be subject to copyright.
1© Springer Nature Switzerland AG 2021
M. Öztürk etal. (eds.), Biodiversity, Conservation and Sustainability in Asia,
https://doi.org/10.1007/978-3-030-59928-7_1
Chapter 1
Biodiversity andEnvironmental
Conservation inPalestine
MazinB.Qumsiyeh andMohammedA.Abusarhan
1.1 Introduction
In the late twentieth century, the conservation of biological diversity became a main
goal of global actions for a sustainable planet. This followed signicant decline in
biodiversity accompanying the industrialization that spread widely in the nineteenth
and twentieth centuries resulting in climate change and habitat destruction (Nurlu
etal. 2008). Two key organizing documents emerged to set the stage for global
actions: the Global Biodiversity Strategy and the Convention on Biological Diversity
(CBD) (both in 1992).
Palestine connects Africa with Eurasia, and it is where the rst humans migrated
out of Africa and also where the rst human agriculture developed. The geologic
history especially the formation of the Great Rift Valley formed varied topography
and evolutionary changes with a rich fauna and ora. There are diverse habitats
covering ve ecological zones (Central Highlands, Semi-coastal Region, Eastern
Slopes, Jordan Rift Valley, and Coastal Regions) and ve phytogeographical areas
(Coastal, Mediterranean, Irano-Turanian, Saharo-Arabian, and Sudanese/Ethiopian)
(Qumsiyeh 1985; Soto-Berelov etal. 2015). Mild weather, rich soils, rich wildlife,
and presence of wild edible fauna and ora allowed humans to go from being
hunter-gatherers to developing an agricultural and nomadic shepherd life
(McCorriston and Hole 1991; Eshed etal. 2004). The transition to agriculture from
hunter-gatherer communities also allowed increase in population and more time for
people to develop civilizations.
Our region has undergone signicant human-induced environmental changes
including those caused by migrations, industrialization, climate change, and coloni-
zation, among others. This had a huge impact on biodiversity, but few studies have
M. B. Qumsiyeh () · M. A. Abusarhan
Palestine Institute for Biodiversity and Sustainability, Bethlehem University,
Bethlehem, Palestine
e-mail: mazin@qumsiyeh.org
2
addressed this. Just this year (2019), we noted numerous ecologically destructive
incidents: trees were uprooted and agricultural lands ravaged by the Israeli army in
Battir and Nahalin in Bethlehem governorate; wastewater dumped by colonists
from “Betar Illit”; seedlings sabotaged by settlers in Burqa, Nablus governorate;
continued environmental siege on Gaza that is devastating the environment; and
much more.1 Israel’s tendency to put polluting industries in Palestinian areas has
unsurprisingly produced negative health consequences for the people living there as
well as for the local ecosystem. For example, signicant genotoxicity is caused by
Israeli industrial settlements on the Palestinian villagers near Salt (Hammad and
Qumsiyeh 2013), and recycling of e-waste that mostly originates in Israel in Idhna
in the Hebron District impacted local health and environment (Khlaif and Qumsiyeh
2017). Also the local people engaged in many practices that impact the environ-
ment. Thus, in this chapter, we review data on what is known about threats to biodi-
versity in Palestine (a small but critical part of the Fertile Crescent) and discuss
opportunities for conservation and sustainable living for both people and fauna
and ora.
1.2 Status ofKey Taxa Related toConservation
The area has been sporadically studied before by visitors to the “Holy land” from
Tristram (1866, 1884) to Morton (1924) to David Harrison in the 1960s (e.g.,
Harrison and Bates 1991). In the 1950s and 1960s, there were some studies of fauna
and ora by the Israelis. The most notable of these was a series called “Fauna
Palaestina” issues by the Israel Academy of Sciences, and good published work
continued to ow into the 1980s (Levy and Amitai 1980; Yom-Tov and Tchernov
1988; Zohary 1973; Werner 1988).
Due to the colonization and occupation, research here still lags behind in
Palestine (Qumsiyeh and Isaac 2012). Among native Palestinian zoologists, Dr.
Sana Atallah (d. 1970) focused on mammals (Atallah 1977, 1978). Key taxa/groups
that are useful for measuring environmental threats and thus important for conserva-
tion status were studied in Palestine. These include mollusks (Amr etal. 2018; Bdir
and Adwan 2011, 2012; Handal etal. 2015, 2016; Heller and Arad 2009), amphib-
ians (Salman etal. 2014), birds (Khalilieh 2016; Awad etal. 2016), and mammals
(Atallah 1977, 1978; Qumsiyeh 1985, 1996; Werner 1988; Harrison and Bates
1991; Whitaker et al. 1994; Qumsiyeh et al. 1996; Qumsiyeh et al. 1998;
Mendelssohn and Yom-Tov 1999; Benda etal. 2010). For example, earlier studies
on the freshwater snails of historical Palestine include those of Tristram (1884) and
Germain and de Kerville (1922) and were supplemented by work of Abdel-Azim
1 See, for example, http://www.lrcj.org/publication-3-1169.html, http://www.lrcj.org/publica-
tion-3-1170.html, http://www.lrcj.org/publication-3-1171.html.
M. B. Qumsiyeh and M. A. Abusarhan
3
and Gismann (1956), Heller etal. (2005), and Handal etal. (2015). Those clearly
show the utility of these taxa in assessing water quality.
So far, 373 bird species belonging to 23 orders, 69 families, 21 subfamilies, and
172 genera have been recorded from the occupied Palestinian areas (Awad etal.
2016). Birds of prey can be of good utility in assessing environmental changes
(because of their position in the food web) (Brett 1988). Amr etal. (2016) showed a
decline in biodiversity in the Bethlehem district evidenced by the study of old and
newer food pellets of the Eagle owl. Saeed and Qumsiyeh (2020) compared records
of birds reported by the rst studies done in the nineteenth century with what is
found today and showed signicant negative trends (related to human effects) such
as the disappearance of the brown shing owl. It is then clear that a study of the
threats to biodiversity is critical.
1.3 Environmental Threats inPalestine
Environmental threats are global in nature but are exacerbated in developing coun-
tries especially in regions of conict. In Palestine, even in ancient times, there is
evidence of Canaanitic villages stripping their populations of gazelles. In the more
modern era, forests in the Eastern Mediterranean region were cut down for house-
hold, industrial, and commercial uses. Under British occupation (1917–1948), and
Israeli and Jordanian rule (>1948), destruction continued, but also interventions that
were supposed to be benecial like forestation were done mostly with European
pine trees (monoculture of Pinus halepensis) (Qumsiyeh 1996).
Under Israeli occupation and colonization, Palestinians were prevented not only
from doing much of their usual agriculture but also from managing lands. Many
forested hills were converted to residential Jewish-only colonial settlements (e.g.,
Jabal Abu-Ghneim became Har Homa colony near Bethlehem) and generated far
more pollution than similar settlements inside Israel.
The modern threats were not unanticipated. For example, Ives (1950) discussed
the land’s capacity and the fact that trends which started in the 1930s if continued
would devastate the area. Not only was he right, but more threats evolved since the
1950s (Qumsiyeh 1996; Tal 2002; Qumsiyeh 2004). Alon Tal acknowledged even
before he wrote his book (2002) that: “We came here to redeem a land and we end
up contaminating it” (Beyer 1998).
The main threats to doing better conservation efforts can be simply categorized
as issues that are peculiarly Palestinian (like occupation/colonization) or global
issues. Anecdotal notes and opinions on the Palestinian environment are not
reviewed in this work (for an example of the genre of this kind of work, see Alleson
and Schoenfeld 2007; Abu Saeh 2012). The ranking of threats to the Palestinian
Environment according to the fth national CBD report is available and seems rea-
sonable though could be adjusted when and if additional data become available
(EQA 2015; Table 1.1). Another report used the Delphi approach to ask some
“experts” what the main threats are and came up with a somewhat different answer
1 Biodiversity andEnvironmental Conservation inPalestine
4
(Abdallah and Swaileh 2011; AlHirsh etal. 2016). But the key threats need not even
be prioritized to be analyzed. AlHirsh etal. (2016) used interviews with selected
individuals involved in environmental issues in Palestine to see what threats are
most prominent to the majority of those individuals.
Here we highlight three of the main threats to the Palestinian environment (cli-
mate change, water and waste water, and occupation/colonization) taken as key
examples that set the stage to discuss interventions. But even here we will have to
be limited because of space.
1.3.1 Climate Change
Climate change has a signicant effect on biodiversity, human health, and sustain-
ability (Harvell etal. 2002; Portnov and Paz 2008; Rinawati etal. 2013; Altay and
Ozturk 2018; Imanberdieva et al. 2018; Ozturk 2018; Ozturk and Altay 2018;
Ozturk etal. 2020), and this requires us to integrate educational, evolutionary, and
ecological responses into models and potential remedies (Settele et al. 2017;
Lavergne etal. 2010; Sternberg etal. 2015). The joint statement by world science
academies warns that “Developing nations that lack the infrastructure or resources
to respond to the impacts of climate change will be particularly affected..”.2 We in
2 http://nationalacademies.org/onpi/06072005.pdf.
Threats
Threat ranking
West Bank Gaza
Habitats fragmentation (due to urbanization, destruction
of forests, climate change, desertification, colonial
activities)
Very High Very High
Desertification and soil erosion (due to overgrazing,
climate change, infrastructure construction etc) High Very High
Urbanization and population growth Very High Medium
Removal of rocks for construction (stone querries etc) Very low Very High
Uprooting trees Low High
Overgrazing Low Very low
Land degradation (poor planning, soil erosion etc.) High Very High
Invasive alien species No data No data
Climate change Low Medium
Overexploitation (including poaching, overfishing etc). High Very High
Pollution (waste water, solid waste, use of chemical
pesticides/insecticides/fertilizers) Medium Very High
Colonial residential and industrial settlements and
associated infrastructure (like the Segregation wall) Very high Very low
Table 1.1 Selected threats to the Palestinian environment (After EQA 2015)
M. B. Qumsiyeh and M. A. Abusarhan
5
countries in the southern Mediterranean areas, the MENA region, will be particu-
larly vulnerable (Sala etal. 2000).
Human-induced climate change will drastically effect the Arab world (Verner
2012). A World Bank study shows impacts including water resource decline will be
drastic by 2040. In the West Bank and Gaza, while demand will double, supply will
shrink dramatically! When coupled with population growth and habitat destruction
(see Table1.1), both the World Bank (Verner 2012) and the UN predict situation to
become unlivable (UN 2012).
Newer models attempt to integrate species’ own responses (ecologically, geneti-
cally, etc.) in predicting changes in species distribution following climate change
and its impact on the habitat (Ozturk etal. 2004, 2012a; Lavergne etal. 2010). But
preliminary data in Palestine in at least one study shows decline in vertebrate biodi-
versity as desertication spread into the Bethlehem district (Qumsiyeh etal. 2014).
1.3.2 Water andLiquid Waste
The situation of water is becoming very critical in the MENA region. While it is
clear how it impacts human health and well-being, it is also critical for the ecosys-
tem. Open water sources if closed off to use only for humans will impact a diversity
of organisms. The government of the state of Israel which controls Palestinian
(native) water claims there is water shortage, but the reality is that there is simply
unequal distribution. For example, Israel diverts and uses most of the water resources
of the Jordan River basin for irrigation farming through the so-called Israel national
water carrier/canal (Elmusa 1998). From 1250 million cubic meters (mcm) per year,
the river’s ow declined to <20mcm (Soffer 1994). Palestinians used 140 pumping
units along the Jordan River before 1967, and all were destroyed or conscated by
the occupation authorities. Now Palestinians use <0.5% of the river basin waters.
After a thorough review of the hydrological data, Elmusa (1998) concluded that:
“Israel takes 80–90% of the freshwater resources of geographic Palestine. … The
disparity in extraction between the two sides has translated into a conspicuous water
gap in all sectors. … The gap is even more conspicuous between the Palestinians
and the Israeli settlers who consume ve to six times as much per capita as do the
Palestinians and are proigate irrigation water users” (Elmusa 1998).
The UN Commission on Human Rights reported in 2000 that:
The Palestinian use of the Jordan River before 1967 was through 140 pumping units. Israel
either conscated or destroyed all of those pumping units. In addition, Israel closed the
large, irrigated areas of the Jordan Valley used by Palestinians, calling them military zones
that later were transferred to Israeli settlers. At present Israel extracts more than 85 per cent
of the Palestinian water from the West Bank aquifers.
Through military orders, all water in the occupied territories is designated “state
owned by Israel” even though this violates the Fourth Geneva Convention (UNEP
2003). Palestine (a state not recognized by Israel as the occupying authority) did
attempt to draft water and other natural resources’ laws. The Palestinian authority
even failed to get Israel to agree to many waste water and solid waste projects.
1 Biodiversity andEnvironmental Conservation inPalestine
6
As Israel takes 91% of the West Bank Water resources, it provides much of it to
illegal settlers (UN Commission of Human Rights 2000). It is obvious that all these
measures contravene International law and conventions such as the Fourth Geneva
Convention and the International Covenant on Economic, Social and Cultural
Rights (Elmusa 1998). Israel also declared places like the Jordan valley closed mili-
tary zones. Vast tracks of Palestinian agricultural lands were thus essentially cons-
cated and many of them turned to Jewish settlements.
The Oslo agreements were supposed to lead to ending the occupation but simply
entrenched it with all attendant strengthening of Israeli control over the natural
resources including water. International treaties and laws pertaining to water were
ignored in deference to “might makes right.” Regardless of political outcomes, there
is simply a very small geographic territory (historic Palestine) with one hydrologi-
cal system (Elmusa 1998). One democratic state ensuring distribution of water to its
citizens based on international guidelines is actually most logical. The situation in
Gaza is now catastrophic and cannot continue (Baalousha 2006; UN 2012). Water
desalination projects as solution in Gaza have their own environmental issues.
The Israeli actions toward water sources have been catastrophic for nature biodi-
versity since the creation of “State of Israel,” starting from drying out al Hula wet-
lands which eradicated life there and not ending with the Red Sea-Dead Sea Canal
project. The latter is a prime environmental problem and should not have been
implemented (the project already started). Its impact in the OPT will be most acutely
felt in the unnatural “replenishment” of the Dead Sea while leaving the Jordan val-
ley essentially dry and with continued environmental deterioration. We did some
work on this, but much more research needs to be done, and the summary of these
things are beyond the scope of this report.
But there is also mismanagement of the shrinking and limited water resources on
the Palestinian side. A decaying water infrastructure is not upgraded because state
funding has other priorities (like security, education, and healthcare). So there is
some loss of water through the existing pipeline structures. In some areas, there is
poor protection to freshwater supplies. For example, in the biodiversity important
area of Al-Bathan near Nablus, the sewage water course merges with the freshwater
spring course just below the picnic and park areas (ARIJ 2015). Further, there is no
organized program to alert tourists to conserve water even as the ministry of tourism
pushes hard to increase number of pilgrims to the Holy Land. Clearly some things
can and should be done regardless of the status of the occupation.
The situation for sewage management in the occupied Palestinian areas is criti-
cal. In Gaza, a signicant portion of the sewage ows untreated to the Mediterranean
Sea. According UNEP (2003), 70% of solid waste in the occupied Palestinian ter-
ritories is organic waste. This is a very high number and one that gives us an oppor-
tunity for signicant reduction via composting to generate fertilizers. Sewage can
also be treated, and other solid waste like metals and plastics and glass can be recy-
cled. Waste water is dumped on some signicant supposedly protected areas like
Wadi Qana, Wadi Nar, and Wadi Far’a (Bathan), around Salt (EQA 2015), and into
the Mediterranean Sea where it is highly damaging to the environment (Akram and
Cheslow 2016).
M. B. Qumsiyeh and M. A. Abusarhan
7
There is a real crisis in logistics and nancing for proper solid waste disposal in
Palestine (Abu Thaher 2005; Al-Khatib et al. 2007). The majority of solid waste
disposed of in Palestinian areas like Nablus is organic which indicates a great poten-
tial for resource utilization such as for composting/fertilizer generation (Al-Khatib
etal. 2010). But as in many developing countries, management of such solid waste
lags behind signicantly (Ahmed and Ali 2004).
1.3.3 Occupation/Colonization
Palestine had an indigenous Canaanitic population going back thousands of years
and living in small village communities with few urbanized areas (like Jerusalem,
Hebron, and Nablus). At the dawn of the industrial revolution, the population was a
few hundred thousand (3% Jewish, 13% Christian, 80% Muslim, 4% other). The
industrial age and improvement in health resulted in population expansion, but the
Zionist project resulted in ethnic cleansing of most of the natives to be replaced by
an immigrant, mostly European-Jewish population (Pappe 2006). Over 500 villages
and towns were destroyed (most in 1948–1950, some in 1967). While Israel was
created on 78% of Palestine, the remaining 22% was occupied in 1967 (Masalha
1992; Qumsiyeh 2004). In 1967, Imwas village was depopulated, and in its place,
Canada Park was built. In all other areas of the occupied territories, forests and
vegetation cover was removed to build the Israeli settlements which now house
hundreds of thousands of Israelis. Simultaneously, rules were introduced that pre-
vented Palestinians not only from doing much of their usual agriculture but also
from managing forested lands or building in open spaces.
Currently nearly one million Israelis live in the occupied West Bank (WB). The
WB is also divided into several categories: Jerusalem annexed to Israel, area C
under Israeli civil and military control, area B under Israeli military control only
(18.3%), and Area A under Palestinian civil and partial security control (17.7%)
(ARIJ 2015). 30% of the territory is designated as closed military zones and “nature
reserves” (these are occasionally reclassied to allow colonization). Israeli colonies
were built on hilltops to t into a pattern as to control the natural resources and
control the native Palestinians (Benvenisti 2002). Environmental and human sus-
tainability were not taken into considerations in these political decisions (ARIJ
2015). Untreated sewage water is discharged by settlers on Palestinian areas (ARIJ
2005; Newman 2009).
Israeli polluting industries were built near Palestinian communities in the occu-
pied territories (due to tax incentives and lax laws). Gishuri Industries as an example
manufactures pesticides and fertilizers next to Tulkarm. Signicant pollution from
this and other companies in this area has damaged citrus and vineyards (ARIJ 2015).
We also showed signicant genotoxic effect of the Barqan Industrial settlement on
Burqeen village (Hammad and Qumsiyeh 2013).
Israel built “bypass” roads and other infrastructures in the occupied areas to
serve the Jewish colonies. Lands were conscated to build these, including extra
1 Biodiversity andEnvironmental Conservation inPalestine
8
“security zones and buffers” around roads, walls, etc. The landscape was severely
damaged; 51.2km2 were destroyed just in 2000 for roads that do not served the local
population. Land that was used by Palestinians or by wildlife thus was urbanized.
Palestinians in the West Bank make 2.5million people living in a built-up area of
367.7km2, a density of 6800 Palestinians per square kilometer which is 10 times
more dense than for Israelis (ARIJ 2015). The disparity between settlers and natives
in land control, economy, and access is also compounded by disparity in use of
natural resources discussed earlier (Gordon 2008).
There are many other issues where the occupation negatively impacts sustainable
development and the environment (MOPAD 2014). For example, tourism industry
was mostly taken over, and it is supporting Israeli economy while negatively impact-
ing the Palestinian economy and the Palestinian environment (Shay 2016; Isaac
etal. 2016). Another example is the destruction of Bedouins life in the Negev (creat-
ing “concentration areas” for them) (Weizman and Sheikh 2015).
Politics trumping facts can be devastating to understanding of issues like envi-
ronment and water. For example, deliberately misstating facts, hiding them, selec-
tivelyusing (mis)information, and much more were done by Israeli ofcials to serve
their political interests in the Jordan River basin (Messerschmid and Selby 2015).
Israel’s unilateral actions of colonial settlement expansion and destruction of native
lives have had devastating impacts on the Palestinian environment and raise signi-
cant questions about the possibility of planning let alone sustainability under occu-
pation (Isaac etal. 2004). There may be a good reason to engage in legal proceedings
that would be backed by good research and enlisting the services of good legal
scholars and lawyers to pursue clams of environmental injustice and damages at
local, national, and international fora.
The term “Green-washing the occupation” comes to mind when we realize that
in many cases Israel takes land on the pretext of protecting it only to build colonies
on it (Etkes and Ofran 2007). Ras Imweis and adjacent areas are a good example of
this (became the settlement Nahal Shiloh). “Nature Reserves” and closed areas
became pretexts for land conscation. Such exploitation was obvious in the
Bethlehem Governorate, when Har Homa settlement was established in 1997 on
Abu Ghneim Mountain (Fig.1.1).
1.4 Biodiversity Conservation Strategies inPalestine
The key vision that drives or should drive environmental conservation in Palestine
as elsewhere should be a vision of a sustainable human population in a sustainable
diverse natural environment. The latter must protect all elements of the ecosystem
including plant-animal interactions. Since the industrial revolution, sustainability of
ecosystems around the world has eroded due to human activity that causes habitat
loss and environmental degradation. In the last few decades and especially with the
growing realization of global human-induced climate change, there has been
increased awareness and efforts focused on environmental conservation and at least
M. B. Qumsiyeh and M. A. Abusarhan
9
trying to halt destruction and mitigate effects with even some efforts going toward
reversal of human-induced habitat changes. Most efforts are focused on in situ con-
servation of natural resources (Adams etal. 2004; AlHirsh etal. 2016).
The Governing Council/Global Ministerial Environment Forum in Cartagena,
Colombia, asked the United Nations Environment Program (UNEP) to look at the
state of the environment in Palestine. The results of a detailed study (UNEP 2003)
led to more work and nally summarized in the Fifth National Report to the
Convention on Biological Diversity (EQA 2015).
In 2015, EQA, through funds from the Belgian Cooperation Program, conducted
a study of rich biodiversity areas. A total of 50 proposed protected areas were listed
in the occupied Palestinian territories (Table1.2); several of them are already listed
as protected or important plant areas. Results of this study excluded some of these
sites, since they are located within towns or cities or used as quarry pits. A detailed
report is still under revision at the EQA.Boundaries of 29 areas were modied;
three were not modied, while 18 were excluded from the proposed list. Two addi-
tional sites were suggested: Dura al Qare’a and Um al Safa 2. We also have a new
study in the Wadi Makhrour area near Bethlehem that proposes it as a protected area
(PIBS unpublished data).
Biodiversity conservation and protected areas in particular are covered by the
National Biodiversity Strategy and Action Plan (NBSAP). The Plan focuses on pro-
tected areas and participation by the local and encourages capacity building in areas
of biodiversity conservation. The Plan also addressed gaps that are very essential to
develop concepts in biodiversity and protected areas conservation. These gaps include
Fig. 1.1 The Israeli colony of Har Homa which was built and is still being expanded on a forested
Palestinian Hill (called Jabal Abu Ghneim)
1 Biodiversity andEnvironmental Conservation inPalestine
10
lack of primary scientic data, information, and documentation on biodiversity in
Palestine and lack of and/or limited human resources. There are very few biologists
especially marine and wildlife biologists and taxonomists, oceanographers, conserva-
tion managers, etc. and adequate legal frameworks and environmental policy and
legal framework on which to base all activities for the conservation and sustainable
use of biodiversity in Palestine, lack of coordination among national and local stake-
holder agencies in biodiversity, and inadequate awareness and commitment to biodi-
versity. The objectives of the NBSAP for Palestine are in line with other countries in
environmental conservation and sustainability. Now the EQA is engaged with us to
build an updated and new NBSAP and produce the Sixth National CBD Report.
The earlier report from the state of Palestine in compliance with CBD listed
many priorities ranging from basic research in biodiversity, threat assessments, bet-
ter private-public relationships, using cultural heritage, better protected area man-
agement, stemming desertication, mitigation and adaptation to climate change,
and habitat restoration (EQA 2015). The report lists in its executive summary 14
recommendations. Here they are paraphrased:
• Collaborative Management of Biodiversity
• Updating NBSAP
• Meet Aichi targets
• Mainstream biodiversity
• Better research to ll the gaps in knowledge
• Emphasize ecosystem services
• Work on areas like poaching (see, e.g., Helal and Khalilieh 2005), wildlife trade
(e.g., Yom-Tov 2003), genetic diversity, biosafety, genetic modied organisms
(GMOs), invasive species, and mitigation and adaptation
• Better investigations and rankings of threats as well as modeling and structuring
responses scientically and with community involvement
The ve NBSAP objectives were identied with very limited progress achieved
since the Fourth National Report. The only thing mentioned elsewhere in the same
report but not clearly mentioned in these ve objectives is the value of doing
Table 1.2 Key biodiversity areas that were listed in the Palestinian territories
Governorate No. Area
Bethlehem 7 Al Jaba’h, Jabal Abu Ghunaim, Mar Saba, Suleiman pools, Wadi Herodian,
Wadi Makhrur, Wadi Fouqin
Hebron 11 Adderat-Yatta, Al Fawwar, Beit Fajjar, Beit Kahil, Beit Umar, Beit Ummar,
Deir Razeh, Ithnah-Souba, Kanar, Tarqoumia, West Karma
Jenin 5 Aqqaba, Kufer El Rai, Quen, Um Al Rihan, Um Al Tut
Jericho 3 Ain Esultan, Deir Hajalih, Wadi Auja
Jerusalem 8 Abu Deis, Anata, east of Aza’ym, Hizma, Mar Elias, Nabi Musa, north Tuur,
beginning of Wadi Ennar
Nablus 6 Aqrabaniya, El Mizrab, Ein Sabastia, Salman Faresi, Talouza, Wadi Faraa
Qalqilya 2 Azzoun, Jayous
Ramallah 6 Al Jalazon, Ain Qinia, Beir Zeit, Jabal El Nijma, Turmus Ayya, Um Safa
Salt 2 Al Matwi, Wadi Esha’ir
M. B. Qumsiyeh and M. A. Abusarhan
11
research; see above also from (EQA 2015). Vulnerable areas are of particular inter-
est for further study because environmental degradation in Palestine has been accel-
erated with industrialization and large-scale deforestation.
In terms of conservation, there are even fewer scientic research studies pub-
lished in the last 25years. However, there were important larger reports that we
considered that contributed to our understanding of environmental issues in the OPT,
including biodiversity conservation. There were of course hundreds of other docu-
ments and research reports consulted during the course of this study (list of refer-
ences cited at the end of the chapter). Two key factors that enter into success of
environmental conservation in any country are economic and social factors. As noted
above, the level of GDP is directly correlated with environmental concern (Mills and
Waite 2009). The 13million Palestinians in the world are now dispersed in many
countries with 7.5million being refugees or displaced people. In historic Palestine,
over 6.2million Palestinians still live, but nearly 30% of them are internally dis-
placed or recognized as refugees. The GDP per capita of Palestinians is 1/8th that of
Israelis who share with them the space of historic Palestine, but this gets more dis-
torted during the cyclical uprisings against the occupation (Hever 2010). This has
impact on environment and R&D (Qumsiyeh and Isaac 2012). For example, accord-
ing to UNEP (2003), the GDP of the OPT which grew at 6% in 1999 shrunk by 6.5%
in 2000 due to Israeli measures in response to the 2000 uprising. Further, there was
a decline in GDP growth in the past few years as population grew while the economy
did not expand (MOPAD 2014). There was some evidence that poorer communities
and countries do worse in protecting their own environments, but this has been chal-
lenged, and richer countries may be fueling their own prosperity via exploitation of
natural resources in poor countries (Mills and Waite 2009).
There has to be benet sharing from conservation and biodiversity. Gorlach etal.
(2011) summarized potential economic benets from environmental conservation
efforts (if successful) in the OPT.Though this benet assessment was mostly based
on little data collected on the ground, it does highlight the signicant potential
impact of saving our environment nancially. Here are examples:
• Air: If air pollution is cut by 50%, modeling suggests premature mortality could
decline by 220 and morbidity by 440 per year. Monetary benet could be of
68million euros per year.
• Water: Improved access to water services could signicantly improve the qual-
ity of life for 1.2million Palestinians. Improved wastewater treatment (perhaps
concomitant with reduction of waste water in general) could have signicant
impacts on biodiversity, groundwater quality, and human health.
• Waste: Reducing solid waste would have signicant impact on air quality, on
environmental health, on human economy, and on biodiversity.
The use of plants and animals for humans is a eld that needs much examination
as it related to environmental conservation directly especially in terms of sustain-
able use of resources (Nurlu etal. 2008; Gucel etal. 2006, 2012; Khan etal. 2014;
Altay etal. 2015; Ozturk etal. 2012b, 2014, 2017a, b). In Palestine as elsewhere,
there is an interest in ethnobotany and ethnozoology (Ali-Shtayeh and Jamous
2006; Ali-Shtayeh etal. 2014; Palevits and Yaniv 2000; Said etal. 2002).
1 Biodiversity andEnvironmental Conservation inPalestine
12
Poverty reduction and environmental conservation are directly linked, and we
are not able to do proper conservation without tackling poverty in developing coun-
tries (Adams et al. 2004; Ozturk and Kebapci 2005; Ozturk etal. 2010; Ozturk
2013). Further it is possible to use socioeconomic incentives at periphery of pro-
tected areas or even allow managed use of natural resources as a form of poverty
reduction which also incentivizes the local people to protect their environment
(Ozturk and Kebapci 2005; Sunderlin etal. 2005; Ozturk etal. 2010).
Modern conservation philosophy argues that the local buy-in is critical for suc-
cess of conservation efforts. We in Palestine certainly need to think strategically
about how people around protected areas are to benet from protection. There are
models in nearby areas, for example, the way the Royal Society for Conservation of
Nature worked with local communities to ensure active buy-in via direct benet
from things like ecotourism and environmentally sensitive agriculture.
Religious attitudes can be of potential use to promote environmental awareness
and conservation. Religious clerks (Muslim and Christian) can introduce many con-
cepts of conservation and environmental practices in the Friday and Sunday ser-
mons. Several authors dealt with the ethical and divine relation of Islam to
environment conservation (Amr and Quatrameez 2002). Islamic teachings are full
of orders and events that encourage conservation as the concept of “Al Himma,” to
save water, clean environment, and many others. Similarly, in Christianity, basic
teachings include many environmentally friendly practices. In Palestine, The Holy
Land, with so many religious connections and about a million devout pilgrims per
year, it is incumbent upon policy makers and stakeholders to research ways to reach
out to those who are religious with the message of environmental conservation.
The Palestinian Environmental Law needs to be updated. Violations of the law
should include higher penalties. Obstacles to implementation include the fact that
most (81%) of the protected areas are in Area C under Israeli rule. For example, the
nascent state of Palestine cannot plan or protect its natural resources including areas
like the unique corridor of Ein Fash’kha to Ein Jedi along the Dead Seaif it cannot
access them (Garstecki etal. 2010; EQA 2015; http://www.nsp.pna.ps/en/). It is also
worth noting that 36.2% of the designated protected areas overlap with Israeli
settlements and 39.5% overlap with closed military areas and bases. Such utiliza-
tion of a protected area conrms that their declaration does not respond to the inter-
national denition of a protected area, which calls mainly for biodiversity
conservation (Ghattas 2008).
Despite all these obstacles, we think some things can still be done. The Palestine
Institute for Biodiversity and Sustainability (PIBS), the Palestine Museum of
Natural History (PMNH), and the Palestine Conservation Botanical Gardens
(PCBG) were started at Bethlehem University with a vision of sustainable human
and natural communities and ecosystems. The mission focuses on research, educa-
tion, and conservation. The motto is RESPECT—for ourselves, for others, and for
the environment. Via working with mainly school children, we do education tailored
to different ages (Figs.1.2, 1.3 and 1.4). We also built educational material via
intensive research to assess need and local cultural peculiarities. For example, we
developed six educational modules in the areas of agriculture, biodiversity, geogra-
M. B. Qumsiyeh and M. A. Abusarhan
13
Fig. 1.2 Children learning via playing, for example, imagining being a scorpion
Fig. 1.3 Museum staff
member (Elias Handal)
with students in show
and tell
1 Biodiversity andEnvironmental Conservation inPalestine
14
Fig. 1.4 Girls at the museum showing their gifts and decorations made from recycled solid waste
Fig. 1.5 One of many locally sensitive educational modules (in this case a poster on biodiversity)
done related to climate change and conservation
phy, energy and transportation, waste and chemicals, and climate change (see the
example in Fig.1.5). PIBS/PMNH annual report is found here: https://www.pal-
estinenature.org/about- us/nal- annual- report.pdf.
For short videos about other activities/accomplishments, please see https://youtu.
be/BPhFLOsEIM0 and https://youtu.be/AZOoOzXU7tQ.
M. B. Qumsiyeh and M. A. Abusarhan
15
1.5 Discussion
Palestine (renamed Israel in 1948) now has over 12 million people. Half the popula-
tion is Israeli-Jewish, and they control 91.7% of the land, and the other half are
native Christians and Muslims who control less than 8.3% of the land. Additionally,
close to 6 million Palestinians live outside the country (mostly refugees). Israel is
trying a three-pronged program: (a) preventing refugees from returning, (b) incen-
tives and other tools to lure in as many Jewish (or even non-Jewish but not native)
immigrants who identify with Zionism, and (c) making life so hard for the remain-
ing Palestinians that they leave (or even outright removing them) (Qumsiyeh 2004).
Environmental destruction is related to instability, inequality of resource distribu-
tion, and habitat destruction in Palestine (Kelly and Homer-Dixon 1996; Qumsiyeh
2013). Solving this requires addressing these issues.
Alatout (2006) showed that differences in perception of power relationships
impact perceptions of issues of environmental justice between Palestinians and
Israelis. Basically those in power view environmental issues in terms of improve-
ments in their quality of life, while Palestinians view them as issues of sovereignty,
property rights, and mere survival.
In the past 25years, there has been a revival of interest in studies of biodiversity
among native Palestinians. Of course we have in no way even approached the level
of publications or interest in nearby countries like Jordan or Israel, but we must
guard against a decline of that interest in biodiversity research seen, for example, in
Israel in association with industrialization (Dayan et al. 2011). We will discuss
below examples of this revival of interest, including the establishment of a number
of programs at universities (e.g., master programs in Environmental Studies at
Al-Quds and Birzeit and the Institute of Biodiversity and Sustainability at Bethlehem
University). But we must also separate scientic work from anecdotal notes and
opinions on the Palestinian environment.
A big challenge to the EQA and relevant agencies working on Palestinian diver-
sity is that there are so few baseline studies on where are the rich biodiversity areas
and what they contain in the OPT (a gap of knowledge). Recent work in the past
5years on protected areas and their buffer zones in Palestinian areas can provide a
model for biodiversity conservation while promoting ecosystem services. Two
prominent examples from our work is Wadi Al-Quff (Qumsiyeh 2016a, b; Qumsiyeh
etal. 2016; Khalilieh 2016) and Wadi Makhrour. Al-Makhrour is the last remaining
biodiversity-rich area in the Bethlehem district, 2.6km2 of natural areas interspersed
with agriculture and rich ora and fauna and an equivalent buffer zone of more than
5km2. It is also one of 13 important bird areas in Palestine rich in cultural heritage,
including old Roman tombs, ancient wells, old Palestinian watchtowers, and a part
which is considered a World Heritage Site by UNESCO.However, no management
plans or conservation programs have been implemented by any organization in the
area. The valley suffers from habitat loss and land fragmentation, causing biodiver-
sity loss, and from challenging livelihood conditions as a result of (among others)
the lack of economic motivations, no subsidies for farming practices, and inadequate
markets for extra production. A project initiated by our institute there showed that
we can use education, permaculture, agricultural, and ecotourism to actually make a
difference even under these difcult circumstances of occupation and colonization.
1 Biodiversity andEnvironmental Conservation inPalestine
16
1.6 Recommendations
1.6.1 Research
Palestine needs scientic data covering all areas relevant to protected areas and
potential protected areas by using the best available data collection methods. We
recommend this effort to collect baseline data be led by qualied academic centers
covering areas like geography, geology, hydrology, fauna, and ora. The only pro-
tected area where such data was collected is Wadi Al-Quff (Qumsiyeh 2016a, b;
Qumsiyeh et al. 2016; Khalilieh 2016). With upward of 48–51 areas in need of
protection, the work ahead of us is daunting and will take a few years. We suggest
prioritizing the work in the next 5years to study Al-Qarn, Wadi Haramya, Wadi
Al-Qelt, Um Al-Tut, and Wadi Qana. The studies must use experts after proper
announcements of funding availability.
1.6.2 Management Plans toDeal withThreats
Management plans must use ecosystem approaches and deal with social, cultural,
and economic issues. Designing Management Plans for protected areas are done by
trained experts (we have so few of those in the Middle East). Thankfully, groups like
the RSCN (Jordan) are willing to help. The conict between EQA and the MOA in
terms of authority over parks should be resolved one way or another. That the EQA
with help of some experts came up with a draft management plan for Wadi Al-Quff
is a rst step. That project costs over $100,000 and 2years of work for just one
locality. The next should be sitting down at high-level government ofcials to decide
how to and who should implement the plan. There is unfortunately a failure to do
that, and instead there is now a plan afoot to transfer the responsibility of Wadi
Al-Quff PA to the municipality of Hebron to manage it. Local municipalities are
subject to various pressures which cannot result in sustainable conservation efforts.
This would be a very bad omen for this rich area with key endangered species like
raptors. It could also set a very bad precedent.
1.6.3 Economy andEcotourism
Strategies for conservation that also enhance local economic development (e.g.
through use of permaculture) must be developed. Much can be done in promoting
tourism even under occupation if partnerships are built such as what happened with
Masar Ibrahim between academia and NGOs. Other possible partnerships are the
ones involving the private sector and civil society groups and the government min-
istries with civil society groups in more ofcial capacities. The most important is to
M. B. Qumsiyeh and M. A. Abusarhan
17
revive and invest in the capacity of a restructured EQA to oversee these partnerships
and ensure outcome-driven projects are implemented without duplication of efforts
and with maximum efciency. Tourism must be developed only if it is sustainable.
We believe in developing areas like agricultural tourism, ecotourism, cultural tour-
ism, and other forms of alternative/sustainable tourism. Similarly, much can be
done to make sure that conservation is benecial to the local community rather than
harmful to their economy.
1.6.4 Conservation Mainstreaming
Knowledge base of conservation issues in Palestine linked to global conservation
efforts (mostly developed by researchers with some support from NGOs and EQA
and MOA) must be expanded. Conservation awareness must be structured in a uni-
ed way to (a) explain what conservation is, (b) why we need it, and (c) how each
of us can affect the change in behavior. Existing ofcials in NGOs, academic insti-
tutions, and governmental bodies must prioritize conservation. In 2005, 170
Palestinian civil society organizations called for using the strategy of boycotts,
divestments, and sanctions as a peaceful non-violent strategy to end the occupation
and achieve other internationally recognized rights of the Palestinian people. Since
then, thousands of NGOs and all major academic institutions in Palestine have
adopted this call (see bdsmovement.net). Credible environmental groups did join
this campaign. Environmentally sensible choices of consumers can also be encour-
aged that are protective of the environment/ethical consumerism (see Dajani and
Isma’il 2014). The EU and other funders must stop any and all efforts to promote
normalization because they do not lead to peace. Peacemaking in situations of
occupation and colonialism has a very well-developed theoretical and practical
body of knowledge that can be evaluated but is beyond the scope of this work.
Further such efforts only make the environmental situation worse by delaying free-
dom and sovereignty for the native people.
Acknowledgments We would like to thank Prof. Zuhair Amr, Elias Handal, Mohammad Najajrah,
and our PIBS team for their support. Thanks are also due to the Environmental Quality Authority
(esp. Dr. Issa Baradiya and Mohammad Mahasne) for their help. Funding for part of the work came
from the City of Geneva, the Darwin Initiative, and the EU Peace Initiative (project Unity and
Diversity in Nature and Society).
References
Abdallah T, Swaileh K (2011) Effects of the Israeli Segregation Wall on biodiversity and environ-
mental sustainable development in the West Bank, Palestine. Int J Environ Stud 68:543–555
Abdel-Azim M, Gismann A (1956) Bilharziasis survey in South-Western Asia; covering Iraq,
Israel, Jordan, Lebanon, Sa’udi Arabia, and Syria: 1950–51. Bull World Health Organization
1 Biodiversity andEnvironmental Conservation inPalestine
18
Abu Saeh Y (2012) The radical transformation of Palestine’s environment: Israel’s occupation is
largely responsible for the pollution and radical transformation of the Palestinian environment.
In: Al Jazeera. http://www.aljazeera.com/indepth/opinion/2012/04/201242811593745665.
html
Abu Thaher A (2005) Solid wastes collection, disposal, and nancial aspects in the West Bank.
Environmental Quality Authority, Ramallah
Adams WM, Aveling R, Brockington D etal (2004) Biodiversity conservation and the eradication
of poverty. Science 306:1146–1149
Ahmed SA, Ali M (2004) Partnerships for solid waste management in developing countries: link-
ing theories to realities. J Habitat Int 28:467–479
Akram F, Cheslow D (2016) Gaza sewage poisons coastline, threatens Israel. In: phys.org. https://
phys.org/news/2016- 05- gaza- sewage- poisons- coastline- threatens.html. Accessed 20 Feb 2019
Alatout S (2006) Towards a bio-territorial conception of power: territory, population, and environ-
mental narratives in Palestine and Israel. Polit Geogr 25:601–621
AlHirsh I, Battisti C, Schirone B (2016) Threat analysis for a network of sites in West Bank
(Palestine): an expert-based evaluation supported by grey literature and local knowledge. J Nat
Conserv 31:61–70
Ali-Shtayeh MS, Jamous RM (2006) Ethnobotany of Palestinian herbal medicine in the northern
West Bank and Gaza strip: review and comprehensive eld study. Biodivers Environ Sci Stud
Ser 4:1–122
Ali-Shtayeh MS, Jamous RM, Abu-Zeitoun SY (2014) National list of medicinal plants in
Palestine-west bank and Gaza strip. Palestine Biodiversity & Environmental Research Center,
Til, Nablus
Al-Khatib IA, Arafat HA, Basheer T etal (2007) Trends and problems of solid waste management
in developing countries: a case study in seven Palestinian districts. Waste Manag 27:1910–1919
Al-Khatib IA, Monou M, Zahra ASFA etal (2010) Solid waste characterization, quantication and
management practices in developing countries. A case study: Nablus District. Palest J Environ
Manag 91:1131–1138
Alleson I, Schoenfeld S (2007) Environmental justice and peacebuilding in the Middle East. Peace
Rev 19:371–379
Altay V, Ozturk M (2018) Potential impact of climate change on relict plant species. In: 2nd inter-
national science conference on “natural sciences, climate & biodiversity”, September 15–17,
2018, Muzaffarabad, Pakistan, 68–69
Altay V, Keskin M, Karahan F (2015) An assessment of the plant biodiversity of Mustafa Kemal
university Tayfur Sokmen campus (Hatay-Turkey) for the view of human health. Int J Sci
Technol Res 1(2):83–103
Amr ZS, Quatrameez M (2002) Wildlife conservation in Jordan: a cultural and Islamic perspec-
tive. Heaven and earth and I: ethics of nature conservation in Asia. Penguin Enterprsie, Delhi,
pp172–184
Amr ZS, Handal EN, Bibi F etal (2016) Change in diet of the Eurasian eagle owl (Bubo bubo)
suggests decline in biodiversity in Wadi Al Makhrour, Bethlehem governorate, Palestinian ter-
ritories. Slovak Raptor J 10:75–79
Amr ZS, Najajreh MH, Zawahrah M etal (2018) Diversity and ecology of the land snails of the
Palestinian territories of the West Bank. Zool Ecol 28:25–35
ARIJ (2005) The nature reserves in light of the Israeli assaults. Applied Research Institute,
Jerusalem
ARIJ (2015) Status of environment in OPT.Applied Research Institute, Jerusalem
Atallah SI (1977) Mammals of the eastern Mediterranean region; their ecology, systematics and
zoogeographical relationships. Säugetierkundliche Mitteilungen 241–319
Atallah SI (1978) Mammals of the eastern Mediterranean region; their ecology, systematics and
zoogeographical relationships. Säugetierkundliche Mitteilungen 1–50
Awad S, Abu Saada RK, Farhoud MH, Khair MI (2016) Checklist of the birds of Palestine. Beit
Jala
Baalousha H (2006) Vulnerability assessment for the Gaza strip, Palestine using DRASTIC.Environ
Geol 50(3):405–414
M. B. Qumsiyeh and M. A. Abusarhan
19
Bdir S, Adwan G (2011) Larval stages of digenetic trematodes in Melanopsis praemorsa snails
from freshwater bodies in Palestine. Asian Pac J Trop Biomed 1:200–204
Bdir S, Adwan G (2012) Three new species of cercariae from Melanopsis praemorsa (L. 1758,
Buccinum) snails in Al-Bathan fresh water body, Palestine. Asian Pac J Trop Biomed
2:1064–1069
Benda P, Lucan RK, Obuch J etal (2010) Bats (Mammalia: Chiroptera) of the Eastern Mediterranean
and Middle East. Part 8. Bats of Jordan: fauna, ecology, echolocation, ectoparasites. Acta Soc
Zool Bohemicae 74:185–353
Benvenisti M (2002) Sacred landscape: the buried history of the Holy Land since 1948. University
of California Press
Beyer L (1998) Trashing the Holy Land. Times Int Mag 62
Brett J (1988) Birds of prey in Palestine. In: 1st Palestinian ecology conference. Department of
Life Sciences, Bethlehem University, 109–112
Dajani M, Isma’il L (2014) Conscious choices: a guide to ethical consumerism in Palestine.
Heinrich-Böll-Stiftung
Dayan T, Ben-Avraham Z, Nathan R etal (2011) Biodiversity research and higher education at the
Research Universities of Israel. Jerusalem
Elmusa SS (1998) Water conict: economics, politics, law and Palestinian-Israeli water resources
EQA (2015) Fifth National report to the convention on biological diversity
Eshed V, Gopher A, Gage TB, Hershkovitz I (2004) Has the transition to agriculture reshaped the
demographic structure of prehistoric populations? New evidence from the Levant. Am J Phys
Anthropol 124:315–329
Etkes D, Ofran H (2007) Construction of settlements and outposts on nature reserves in West Bank
Garstecki T, Al-Rabi T, Mahassneh M, Mezyed B (2010) Assessment of some Palestinian nature
reserves. IUCN
Germain L, de Kerville HG (1922) Mollusques terrestres et uviatiles de Syrie. J.-B.Baillière et ls
Ghattas R (2008) Beyond the natural scenes of Palestinian nature reserves. 34–39
Gordon N (2008) From colonization to separation: exploring the structure of Israel’s occupation.
Third World Q 29:25–44
Gorlach B, Möller-Gulland J, Bar-On H, Atrash I (2011) Analysis for European neighbourhood
policy (ENP) Countries and the Russian Federation of Social and Economic Benets of
Enhanced Environmental Protection
Gucel S, Gokcekus H, Ozturk M (2006) Biodiversity of Northern Cyprus and its conservation
strategies. Int. Meeting, October, 2006, Foca, Turkey
Gucel S, Kadis C, Ozden O etal (2012) Assessment of biodiversity differences between natural
and articial wetlands in Cyprus. Pak J Bot 44:213–224
Hammad KM, Qumsiyeh MB (2013) Genotoxic effects of Israeli industrial pollutants on residents
of Bruqeen village (Salt district, Palestine). Int J Environ Stud 70:655–662
Handal EN, Amr Z, Qumsiyeh MB (2015) Some records of freshwater snail from the occupied
Palestinian territories. Jordan J Nat Hist 2:23–29
Handal EN, Amr ZS, Qumsiyeh MB (2016) Some records of reptiles from the Palestinian territo-
ries. Russ J Herpetol 23:261–270
Harrison DL, Bates PJJ (1991) The mammals of Arabia, 2nd edn. Harrison Zool Museum Publ
Sevenoaks, Kent
Harvell CD, Mitchell CE, Ward JR etal (2002) Climate warming and disease risks for terrestrial
and marine biota. Science 296:2158–2162
Helal H, Khalilieh A (2005) National report on hunting. Unpublished report to the EU
Heller J, Arad Z (2009) Land snails of the land of Israel: natural history and a eld guide. Pensoft
Publ 144:229–260
Heller J, Mordan P, Ben-Ami F, Sivan N (2005) Conchometrics, systematics and distribution of
Melanopsis (Mollusca: Gastropoda) in the Levant. Zool J Linnean Soc 144(2):229–260
Hever S (2010) The political economy of Israel’s occupation. Pluto Press, London
Imanberdieva N, Imankul B, Severoğlu Z etal (2018) Potential impacts of climate change on plant
diversity of Sary-Chelek biosphere Reserve in Kyrgyzstan. In: Egamberdieva D, Ozturk M
(eds) Vegetation of Central Asia and environs. Springer Nature, Cham, pp349–364
1 Biodiversity andEnvironmental Conservation inPalestine
20
Isaac J, Rishmawi K, Safar A (2004) The impact of Israel’s unilateral actions on the Palestinian
environment. Appl Res Institute- Jerusalem
Isaac R, Hall CM, Higgins-Desbiolles F (eds) (2016) The politics and power of tourism in
Palestine, NewYork
Ives RL (1950) The Palestinian environment. Am Sci 38:85–104
Kelly K, Homer-Dixon T (1996) Environmental scarcity and violent conict: the case of Gaza
Khalilieh A (2016) Avifaunal baseline assessment of Wadi Al-Quff protected area and its vicinity,
Hebron, Palestine. Jordan J Nat Hist 3:58–69
Khan MA, Boer B, Ozturk M etal (eds) (2014) Cash crop halophytes and biodiversity conserva-
tion, Sabkha ecosystems IV: (Tasks for vegetation science 47). Springer, NewYork. 339p
Khlaif N, Qumsiyeh MB (2017) Genotoxicity of recycled electronic waste in Idhna, Hebron
District, occupied Palestinian territory: a case-controlled study. Intern J Environ Stud 74:66–74
Lavergne S, Mouquet N, Thuiller W, Ronce O (2010) Biodiversity and climate change: integrating
evolutionary and ecological responses of species and communities. Annu Rev Ecol Evol Syst
41:321–350
Levy G, Amitai P (1980) Fauna Palaestina, Arachnida I: Scorpiones. Israel Academy of Sciences
and Humanities
Masalha N (1992) Expulsion of the Palestinians: the concept of “transfer” in Zionist political
thought, 1882–1948. Institute for Palestine Studies
McCorriston J, Hole F (1991) The ecology of seasonal stress and the origins of agriculture in the
near east. Am Anthropol 93:46–69
Mendelssohn H, Yom-Tov Y (1999) Mammalia of Israel. Israel Academy of Sciences and
Humanities
Messerschmid C, Selby J (2015) Misrepresenting the Jordan River basin. Water Altern 8:258–279
Mills JH, Waite TA (2009) Economic prosperity, biodiversity conservation, and the environmental
Kuznets curve. Ecol Econ 68:2087–2095
MOPAD (2014) State of Palestine National Development Plan 2014–2016. Ministry of Planning
and Administrative Development
Morton KJ (1924) The Dragon-ies (Odonata) of Palestine, based primarily on collections made
by Dr. P.A. Buxton, with Notes on the Species of the Adjacent Regions. Trans R Entomol Soc
London 72:25–44
Newman D (2009) In the name of security: in the name of peace- environmental schizophrenia
and the security discourse in Israel/Palestine. In: Brauch HG etal (eds) Facing global envi-
ronmental change. Hexagon series on human and environmental security and peace. Springer,
Berlin/Heidelberg
Nurlu E, Erdem U, Ozturk M etal (2008) Landscape, demographic developments, biodiversity and
sustainable land use strategy: a case study on Karaburun Peninsula, Izmir, Turkey. In: Petrosillo
I etal (eds) Use of landscape sciences for the assessment of environmental security. Springer,
Dordrecht, pp357–368
Ozturk M (2013) Biodiversity and conservation strategies. Application of frontier technologies
in documentation and conservation of biodiversity and climate change, 29–30 November,
Shaheed Benazir Bhutto University, Pakistan
Ozturk M (2018) Biodiversity and climate change: our home is on re. In: 2nd international
science conference on “natural sciences, climate & biodiversity”, p68, September 15–17,
Muzaffarabad
Ozturk M, Altay V (2018) Impact of climate change on sea level, bioresources, biodiversity,
marine invasive species, ecology and food web: Past, present, and future. Understandıng the
Problems of Inland Waters: Case Study for the Caspian Basin (UPCB), p30–34, 12–14 May,
Baku, Azerbaijan
Ozturk M, Kebapci U (2005) Biodiversity & Conservation: past, present and future. Xth EURECO
European ecological congress, 8-13 November, Kusadasi, p9
Ozturk M, Parks CR, Coskun F et al (2004) Vanishing tertiary genetic heritage in the East
Mediterranean, Liquidamber orientalis Mill. Environ Forensic 10(4):6–8
M. B. Qumsiyeh and M. A. Abusarhan
21
Ozturk M, Aksoy A, Gucel S, Altundag E (2010) Biodiversity & conservation-a case study from
Europe & Turkey. In: Bhatti R, Soomro SA (eds) Proceedings of 2nd international conference
“Biodiversity is our life” (IC Biour-life). Center for Biodiversity & Conservation, Shah Abdul
Latif University, Khairpur, pp1–12
Ozturk M, Gucel S, Altay V, Altundag E (2012a) Alliums, an underutilized genetic resource in the
East Mediterranean. Acta Hort (969):303–309
Ozturk M, Kebapci U, Gucel S etal (2012b) Biodiversity & land degradation in the lower Euphrates
subregion of Turkey. J Environ Biol 33(Suppl):311–323
Ozturk M, Altay V, Gucel S, Guvensen A (2014) Halophytes in the East Mediterranean-their
medicinal and other economical values. Sabkha ecosystems. Vol. IV: Cash crop halophyte and
biodiversity conservation tasks for vegetation science, Vol. 47, Springer, Dordrecht, p247–272
Ozturk M, Altay V, Gonenç TM (2017a) Herbal from high mountains in the East Mediterranean.
In: Bhojraj S etal (eds) Drug discovery from herbs– approaches and applications. DAYA
Publishing House, New Delhi, pp327–367
Ozturk M, Altay V, Gucel S, Altundag E (2017b) Plant diversity of the drylands in Southeast
Anatolia-Turkey: role in human health and food security. In: Ansari AA, Gill SS (eds) Plant
biodiversity: monitoring, assessment and conservation. CABI, Wallingford, pp83–124
Ozturk M, Egamberdieva D, Milica P (2020) Biodiversity and biomedicine-our future. Academic
Press is an imprint of Elsevier, London. 600p
Palevits D, Yaniv Z (2000) Medicinal plants of the Holy Land. Modan Publishing House
Pappe I (2006) The ethnic cleansing of Palestine. Oneworld Publication, Oxford
Portnov BA, Paz S (2008) Climate change and urbanization in arid regions. Ann Arid Zone 47:457
Qumsiyeh MB (1985) The bats of Egypt. Texas Tech Press
Qumsiyeh MB (1996) Mammals of the holy land. Texas Tech University Press
Qumsiyeh MB (2004) Sharing the land of Canaan: human rights and the Israeli-Palestinian strug-
gle. Pluto Press, London
Qumsiyeh MB (2013) The coming environmental Nakba. In: The third Palestinian environmental
awareness and education, conference. EEC, Bethlehem, pp57–59
Qumsiyeh MB (2016a) Fauna of Wadi Al-Quff protected area: amphibians, reptiles and mammals.
Jordan J Nat Hist 3:70–79
Qumsiyeh MB (2016b) Invertebrate Fauna of Wadi Al-Quff protected area, Palestine. Jordan J Nat
Hist 3:80–92
Qumsiyeh MB, Isaac J (2012) Research and development in the occupied Palestinian territories:
challenges and opportunities. Arab Stud Q 34:158–172
Qumsiyeh MB, Amr ZS, Budari AM (1996) Status and conservation of Artiodactyla (Mammalia)
in Jordan. Mammalia:417–430
Qumsiyeh MB, Amr ZS, Al-Oran RM (1998) Further records of bats from Jordan and a synopsis.
Turkish J Zool 22:277–284
Qumsiyeh MB, Zavala SS, Amr ZS (2014) Decline in vertebrate biodiversity in Bethlehem,
Palestine. Jordan J Biol Sci 7:01–107
Qumsiyeh MB, Khalilieh A, Albaradeiya IM, Al-Shaikh B (2016) Biodiversity conservation of
Wadi Al-Quff Protected area (Central Palestine): challenges and opportunities. Jordan J Nat
Hist 3:6–24
Rinawati F, Stein K, Lindner A (2013) Climate change impacts on biodiversity-the setting of a
lingering global crisis. Diversity 5:114–123
Saeed R, Qumsiyeh MB (2020) Are 19th century studies relevant to understanding changes in
raptor bird fauna in the Fertile Crescent? An example from Tristram’s work. Sandgrouse (J
Ornithol Soc Middle East) 42:69–77
Said O, Khalil K, Fulder S, Azaizeh H (2002) Ethnopharmacological survey of medicinal herbs in
Israel, the Golan Heights and the West Bank region. J Ethnopharmacol 83:251–265
Sala OE, Chapin FS, Armesto JJ etal (2000) Global biodiversity scenarios for the year 2100.
Science 287:1770–1774
1 Biodiversity andEnvironmental Conservation inPalestine
22
Salman I, Salsaa M, Qumsiyeh M (2014) Distribution and cytogenetics of amphibians from the
occupied Palestinian territories (West Bank of Jordan). Jordan J Nat Hist 1:116–130
Settele J, Hammen V, Hulme P etal (2017) Alarm: assessing large-scale environmental risks for
biodiversity with tested methods. GAIA Ecol Perspect Sci Soc 14:69–72
Shay T (2016) The Ethnocracy of the Palestinian urban space and the indigenous approach: praxis
and theory. Archaeologies 12:73–90
Soffer A (1994) The relevance of Johnston plan to the reality of 1993 and beyond. In: Isaac J,
Shuval H (eds) Water and peace in the Middle East. Elsevier, Amsterdam
Soto-Berelov M, Fall L, Falconer E, Ridder E (2015) Modeling vegetation dynamics in the south-
ern Levant through the bronze age. J Archaeol Sci 53:94–109
Sternberg M, Gabay O, Angel D etal (2015) Impacts of climate change on biodiversity in Israel:
an expert assessment approach. Reg Environ Chang 15:895–906
Sunderlin WD, Angelsen A, Belcher B etal (2005) Livelihoods, forests, and conservation in devel-
oping countries: an overview. World Dev 33:1383–1402
Tal A (2002) Pollution in a promised land: an environmental history of Israel. Univ of California
Press
Tristram HB (1866) Report on the mammals of Palestine. Proc Zool Soc London 36:84–93
Tristram HB (1884) The survey of Western Palestine: the fauna and ora of Palestine. Committee
of the Palestine Exploration Fund
UN (United Nations) (2012) Gaza in 2020. A liveable place?
UN Commission on Human Rights (2000) Report on the situation of human rights in the Palestinian
territories occupied since 1967/submitted by Giorgio Giacomelli, Special Rapporteur, pursuant
to Commission on Human Rights resolution 1993/2 A, 15 March
UNEP (2003) Desk study on the environment in the occupied Palestinian territories
Verner D (2012) Adaptation to a changing climate in the Arab countries: a case for adaptation
governance and leadership in building climate resilience. The World Bank, Washington, DC
Weizman E, Sheikh F (2015) The conict shoreline: colonialism as climate change in the Negev
Desert
Werner YL (1988) Herpetofaunal survey of Israel (1950-85), with comments on Sinai and Jordan
and on zoogeographical heterogeneity. Monogr Biol 62:355–388
Whitaker JO, Shalmon B, Kunz TH (1994) Food and feeding habits of insectivorous bats from
Israel. Zeitschrift fur Saugetierkd 59:74–81
Yom-Tov Y (2003) Poaching of Israeli wildlife by guest workers. Biol Conserv 110:11–20
Yom-Tov Y, Tchernov E (eds) (1988) The zoogeography of Israel: the distribution and abundance
at a zoogeographical crossroad. Monographiae Biologicae
Zohary M (1973) Geobotanical foundations of the Middle East
M. B. Qumsiyeh and M. A. Abusarhan