research proposal prepared by: rohana … › ismail › files › 2018 › 06 › river...river...
TRANSCRIPT
1
RIVER DEVELOPMENT SHAPED BY COMMUNITY RESILIENCE THROUGH
CULTURAL ECOSYSTEM SERVICES IN MALAYSIA URBAN
NEIGHBOURHOOD
RESEARCH PROPOSAL
PREPARED BY:
ROHANA BINTI MOHD FIRDAUS
PhD CANDIDATE (PBE173062)
SUPERVISOR:
ASSOC. PROF. DR. MOHD HISYAM BIN RASIDI
CO-SUPERVISOR:
DR. MUHAMMAD FARID AZIZUL BIN AZIZUI
PROF. DR. ISMAIL BIN SAID
FACULTY OF BUILT ENVIRONMENT
UNIVERSITI TEKNOLOGI MALAYSIA
81310 SKUDAI, JOHOR
20 MAY 2018
2
1.0 Research Title
River Development shaped by Community Resilience through Cultural Ecosystem
Services in Malaysian Urban Neighborhood
2.0 Research background
Generally, urbanization has become one of the global issue that faced by multiple
rising countries which threaten the importance of urban river in many aspects (Deng
& Xu, 2018). With human as one of the drivers, it has led more destruction of
communities than the natural catastrophes and with environmental threats as well,
many communities have become increasingly suffering the social, political, cultural
and economic disturbance which threatens their survivability (Wilson, 2012);
especially the community nearby the urban river.
Urban river is one of the natural resources that possess many benefits to both human
(Johnson, Bell, & Leahy, 2018) and nature since history whereby major of cities
were built and developed by the riverside (Baschak & Brown, 1994). Urban river is
one of the communal spaces; that offers green space to maximize the level
biodiversity and improve psychology of human being in urban area (Southon,
Jorgensen, Dunnett, Hoyle, & Evans, 2018). However, the appreciation value toward
urban river has been degraded by the development that has turned their back to the
river (Eric, 2018). This has result the disappearance of river in urban neighborhood
accelerated by issue tackled by local authorities or stakeholders are addressed at the
wrong spatial scale (Palmer & Filoso, 2009) with the wrong problems and measures
(González del Tánago, García de Jalón, & Román, 2012). Nevertheless, river
development in urban area has gain attention in these past few years due to the
impact of urbanization that degrade the urban river (Prominski, Stokman, & Zeller,
2012). Due to unsustainable planning and irresponsible human activities, the urban
river has been degraded in many aspects such as its water quality (e.g.: Brotons and
Mallari (2016); Chan, Abdullah, Ibrahim, and Ghazali (2003); Lah, Park, and Cho
(2015)) , river function in flood mitigation (e.g.: Chan et al. (2003); Deng and Xu
(2018)), aquatic ecosystem (e.g.: Everard and Moggridge (2012); Steward, Negus,
3
Marshall, Clifford, and Dent (2018)) and aesthetic value (e.g.: Chen, Hua, Liekens,
and Broekx (2018); Junker and Buchecker (2008); Asakawa, Yoshida, and Yabe
(2004); Plieninger et al. (2015)).
Figure 2.1: Yamuna River, India; Cittarum River, Indonesia; Marilao River,
Philippines; respectively (Source: https://helpsavenature.com/top-ten-most-polluted-
rivers-of-world)
Figure 2.1 shows the top rank of most polluted river in the world which as a result
from serious impact of urbanization to the urban river. These impacts also influence
the community resilience in which according to Pelling (2003), the community
survival is threatening their community resilience through social political, cultural
and economic. In short, community resilience is defined as the capacity to adapt with
the change (Magis, 2010). Community resilience is needed to ensure the community
able to adapt in urban stress and live sustainably with unexpected change. There are
drivers that influence the community resilience which will depend on the river
development. The drivers are influence by social memory which establish a path
dependency of community to be resilient in certain situation (Wilson, 2012).
According to Blignaut, Wit, and Zy (2011), community possess the moral, spiritual,
educational, aesthetic-desired, place-based, and other values towards the urban
environment which influence their attitudes toward Ecosystem Services. Ecosystem
Services is defined as the benefits of people gain from the ecosystem. According to
Blignaut et al. (2011), there are four major are services within Ecosystem Services
namely provisioning services, regulating services, habitat or supporting services, and
cultural services. It has been highlighted by Haase et al. (2014) and Vollmer,
Prescott, Padawangi, Girot, and Grêt-Regamey (2015) that Cultural Ecosystem
Services are the least explored and seldom considered in research because of its
intangible dimension. According to Hassan, Scholes, Ash, Condition, and Group
4
(2005), Cultural Ecosystem Services is commonly defined as the ‘non-material
benefits people obtain from ecosystems through spiritual enrichment, cognitive
development, reflection, recreation, an aesthetic experience, including knowledge
systems, social relations, and aesthetic’. In relation to this research, it is seen that
community resilience is associated with Cultural Ecosystem Services as both are
benefits the community through ecology and environment; in context of river
development in urban neighborhood. Within Malaysia context, it is highlighted by
Chan (2009) that most of the laws and rules on water in Malaysia has failed to
underline the social aspect.
3.0 Problem statement
The deterioration of river persists despite the river development received the
attention for sustainable urban development. The urbanization is caused by
anthropogenic activities which have impacts on land use pattern that threaten the
river (Weil et al., 2018) and resulting the effect on community resilience due to the
river degradation. According to Lerch (2015), the communities and challenges faced
are dynamic. Thus, the impact of community resilience is measured through the
ability to adapt with the changing (Cutter et al., 2008) because the adaptation is an
ongoing process. It will never reach maximum resilience but can only strive to
maximize the resiliency (Wilson, 2014). However, their adaptation is toward the
issue can be threatening and opposing to sustainable living. This is linked with the
urban community whereby they did not have the awareness to be resilient in
sustainable ways. But, resilience is only visible, or revealed, after the occurrence of
an adversity (Schipper & Langston, 2015). This suggests that the adversity is one of
the trigger to the community resilience. In this research, the trigger is referring to the
river development in which focusing on Cultural Ecosystem Services.
In regards to Malaysia context, the river development received well attention since in
late 1990s studied mostly by Chan (1998). He highlighted the issues on protection of
water resource, prevention of water pollution, and treatment of water supply. Despite
the effort on water management by government, the government has failed to
underline the social aspect toward human responsibilities in water management and
this is shown through the government decision in using a top-down approach
5
whereas this approach has been proved to be ineffective in many countries (Chan,
2009). Community resilience involves the social aspect to participate in river
development. This shows that Malaysia is lacking in term of community resilience
perspective which some development failed to underline social aspect (Chan, 2009).
Figure 3.1: According to Kasnoon (2003) from Astro Awani, these are 3 out 5 most
polluted rivers in Malaysia namely Klang River in Selangor, Tebrau River in Johor
and Penang River in Penang, respectively (Source: Astro Awani)
Figure 3.1 shows that the water stressed through the polluted river such as in Klang
River in Selangor, Tebrau River in Johor and Penang River in Penang. According to
the Laporan Tahunan JPS 2016, the number of rivers in Malaysia has been increasing
up to 120 by 2002 and out of that only 30 are categorized as clean by the Department
of Environment Malaysia. It has been detected during in early 2000s, 55 rivers has
exceed its limit after receiving pollutants and thus categorized as polluted. This has
the relationship with the evolution of river; previously, Malaysian’s rivers begin with
settlement by riverside because of the proximity to water supply, function in
transportation, source of food and power generation (Chan et al., 2003). However,
river also become one of the easy conduit for human to discharge waste which has
degrade the value of river, especially in urban context because of the many land uses
developed discharge their harmful waste into the river without treatment (Chan et al.,
2003). This shows the action comes from community decision making which has
lack of awareness toward the river development.
6
4.0 Research Gap
Research on river development has been increasing due to the need of sustainability
caused by the threats from urbanization. Table 4.1 shows studies on river
development have been focusing on many aspects that involve environmental,
economy, politic and social aspect as well.
Table 4.1: Summary of related studies on river development
Authors (years) Concerns/ Issues Explanation
Eze and Knight (2018);
Brierley, Fryirs, Outhet,
and Massey (2002)
Physical of river
profile The river’s fluvial system.
Vollmer et al. (2015);
Kumar, Masago, Mishra,
and Fukushi (2018); Liu,
Shen, Yan, and Yang
(2018); Solins, Thorne,
and Cadenasso (2018)
Ecology of river
and water quality
The riparian plantings’ role in
providing habitat for the aquatic
and improve the river hygienic
environment.
van den Brandeler, Gupta,
and Hordijk (2018); Weil
et al. (2018); Lah et al.
(2015); Chan (2009)
Urban water and
river management
to sustainability
Involves urban planning,
economy and politics as well that
ensure the river and urban
sustainability.
Chen et al. (2018);
Asakawa et al. (2004);
Masud, Moni, Azadi, and
Van Passel (2018);
River development
and Ecosystem
Services
Include human value in river
development that associated with
Ecosystem Services such as
Md. Yassin, Eves, and
McDonagh (2010); Latip,
Shamsudin, and Liew
(2012)
Evolution of river
and waterfront
The transformation of river into a
waterfront for communal uses.
Kondolf and Pinto (2017);
Everard and Moggridge
(2012); Darby and Sear
(2008); Brotons and
Mallari (2016); Gregory
(2006); Chan et al. (2003)
River development
and social aspect
The integration between
community and river environment
such as community’s benefits,
interaction and participation.
Furuta and Shimatani
(2017); Deng and Xu
(2018); (Patel & Gleason, 2018)
River and disaster
recovery
The river used as flood mitigation
and community is highlighted on
the emergency management through the river development.
From the Table 4.1, it shows there is lacking of research on river development
shaped by community resilience. It is also mentioned by Haase et al. (2014) that
Cultural Ecosystem Services is the least explored. This is due to its intangible
7
dimension, non-material benefits and subjective characteristic (Cortinovis &
Geneletti, 2018). Thus, this research aims to investigate the river development
shaped by community resilience by taking Cultural Ecosystem Services as the
landscape perspective.
5.0 Research question
The research questions for this research are:
(a) How the community adapt to the river development shaped by its resilience
through Cultural Ecosystem Services in urban neighbourhood?
(b) Why does community in urban neighbourhood degrade the river?
(c) What are the practices that affecting the community resilience through Cultural
Ecosystem Services within river development in urban neighbourhood?
(d) How aesthetic as cultural ecosystem service gives impact to the community
resilience within river development in urban neighbourhood?
6.0 Research aim
The aim of this research is to investigate how the river development shaped by
community resilience through Cultural Ecosystem Services in Malaysia urban
neighbourhood.
7.0 Research objectives
To achieve the aim, the following objectives are formulated:
(a) To identify factors of community resilience in urban neighbourhood that shapes
river development through Cultural Ecosystem Services;
(b) To examine the level of community resilience toward river development through
Cultural Services in urban neighbourhood; and
(c) To determine the effect of Cultural Ecosystem Services toward community
resilience within river development in urban neighbourhood.
8
8.0 Scope of research
This research will be conducted at Sembulan River Park in Kota Kinabalu Sabah; an
urbanized area which is majorly consists of commercial, industrial and urban
residential uses. This research covers the urban community that lives nearby and use
Sembulan River Park including the squatter settlement. In regards to the Sembulan
River Park, it has been developed through beautification approach but according to
Eric (2018) who design the river park said the design has failed. One of the factors to
the failure was said social aspect. The urban community’s knowledge will be tested
to measure the awareness of the community. Both knowledge (Berkes, Colding, and
Folke (2003); Gunderson, Pritchard, and Environment (2002)) and awareness
(Hunter, 2011) will have influence to their perception (Gregory (2006); Costello,
Johns, and Guilfoyle (2007)) and acceptation (Cha, Shim, and Kim (2011); Costello
et al. (2007)). Thus, it forms their stewardship (Ahmed, Seedat, Niekerk, and
Bulbulia (2004); Davis, Cook, and Cohen (2005)) of the community that shapes their
resiliency.
9.0 Assumption
Due to previous river developments that lack of consideration in social aspect
(Chan, 2009), it has continuously influence the community resilience (Hunter, 2011).
Thus, the river in urban neighborhood is influenced by the community resilience.
This lead to the assumption of river development is worsened by the community
nearby the river that has lack sense of appreciation toward the river development.
This can be seen from the lack of visual attractiveness (derived from aesthetic in
Cultural Ecosystem Services) in the river development shaped by community
resilience.
10.0 Significance of research
This research is significant by responding to the failure of underlining the social
aspect and considers the community resilience through Cultural Ecosystem Services
within river development in urban neighborhood context. The outcome of this
research is a framework on river development that considers the community
9
resilience to ensure the sustainability of the river is maintained by the community
itself. It uses the aesthetic as one of the functions to initiate the community’s
awareness toward sustainability. Thus, it helps the river to be able to become self-
maintain.
11. Literature review
11.1 River development
The topic in regards to human role in changing the river was initiated by Lane in
1955 and 1956 by Strahler. It is supported by Maya et al. (2011) that human being is
the most intensive influence on river. River is one of open spaces; that offers green
space to maximize the level biodiversity and improve psychology of human being in
urban area (Southon et al., 2018). Urban area is defined as the area with high
biodiversity whereby human tend to establish their settlement nearby their natural
resources (Cincotta et al., 2000; Luck, 2007; Macdonald et al., 2008). However, the
appreciation value toward urban river has been degraded whereby the urban
developments have turned their back to the water bodies and some developments
treat it as a drain (Prominski et al., 2012). This is accelerated by the land use pattern
change due to community’s need for built up area; also known as land expansion
(Zhifang Wang, 2018), it results the lack of open spaces and water bodies. The lack
of open spaces is an additional factor for river corridor to deteriorate further
(Asakawa et al., 2004). The deteriorating of river influences its behaviour as a
natural water body and negatively affect the aquatic ecosystem (Eze & Knight,
2018). In addition, due to unsustainable planning and irresponsible human activities,
the urban river corridor has been degraded in aspect of water quality (e.g.: Brotons
and Mallari (2016); Chan et al. (2003); Lah et al. (2015)) , river function in flood
mitigation (e.g.: Chan et al. (2003); Deng and Xu (2018)), aquatic ecosystem (e.g.:
Everard and Moggridge (2012); Steward et al. (2018)) and aesthetic value (e.g.: Chen
et al. (2018); Junker and Buchecker (2008); Asakawa et al. (2004); Plieninger et al.
(2015)).
Nevertheless, river development in urban area has gain many attentions in these past
few years due to the impact of urbanization that degrade the urban river (Prominski
10
et al., 2012). The urbanization has become one of global issue that faced by multiple
rising countries which threaten the importance of urban river in many aspects such as
flood risk, quality of water and ecosystem (Deng & Xu, 2018). Urban river is one of
the natural resources that possess many benefits to both human (Johnson et al., 2018)
and nature since history. Importance of river includes microclimate regulation, clean
water supply, and biodiversity enhancement (Eze & Knight, 2018) as well flood
mitigation function, transportation, riparian habitat, and aesthetic value. Yet, in most
of urban area, the river has been hardened and straightened due to rapid urbanization
until the volume of water can be estimated from its trapezoidal shape and river length
(Deng & Xu, 2018). This shows serious impact of urbanization to the urban river.
Thus, why does the human continues its anthropogenic activities that threatened the
natural resource; urban river?
11.1.1 River profile
According to Chapter 8 of Fluvial Geomorphology in Watershed Science (2012),
fluvial geomorphology is the study of stream’s form and function and its interaction
with the landscape. It is related to the river whereby the fluvial itself is referred as the
processes of running waters which associated within river context; whereas ‘geo’ is
known to refer to earth and ‘morphology’ refers to the form, shapes or structure.
According to Eze and Knight (2018), fluvial geomorphology affect (a) characters, (b)
evolution, (c) behaviour, of biophysical interaction within catchment and recover
potential.
11.1.2 Challenges (Maintaining natural state, multiple roles, complexity,
uncertainty, and sustainability)
Within river development, the challenges become more demanding due to the
increase of complexity within the development itself and community too (van den
Brandeler et al., 2018). It has been noticed one of the challenges in river
development these days is the idea to maintain natural state of river (Eze & Knight,
2018). Thus, the understanding of river behaviour is vital to implement the solution
in development (Franchis, 2014). Previously, most river developments are ad hoc to
single driver or primary outcome only such as water quality. Nowadays, with the
11
urbanization and competing users has become two of the main concerns in
development, multiple requirements are needed (Palmer, Hondula, & Koch, 2014).
For example, a river development that could have multiple roles includes the water
quality, amenities enhancement and flood protection (Liao, 2013). In term of
complexity and scale challenge, it is imposed mostly by the government and
community as well (Speed et al., 2016). In simple words, if the government provide
solution to certain issue in regard river pollution; it is unlikely the community have
the capacity to adapt with the solution. Thus, from this it leads to the increasing of
uncertainty in river development.
According to (Saxton, 2013), river development must allow shift in human value and
belief system. This is seen as to relate with the community resilience. Community
adaptation with the disturbance is a never ending process as mentioned by Davies
(1995), thus the human value and belief system is always changing as well
responding to the development and environment. Furthermore, the challenge toward
ensuring the sustainability of river development is also vital to have the consideration
of social capital (Western, Stimson, Baum, & Van Gellecum, 2005), economic
capital (Adger, 2000), and environment capital (Magis, 2010) which form the
community resilience to ensure the sustainability. However, it is not easy to achieve
the community resilience as there are drivers that influence the community from
achieving sustainable living environment.
11.1.3 River in Malaysia (Overview)
Within Malaysia’s context, it has been detected there is 150 rivers in Malaysia in
2003 and out of that number, it found that 25 experienced water stress and overtime,
the number has increased to 55 which has exceed water limit with heavy metal
contamination (Chan et al., 2003). Data provided by Department of Environment
Malaysia from Laporan JPS 2016 state that there are an increasing number of rivers
that has been monitored throughout Malaysia since 1987 to 2002 from 91 to 120
rivers respectively.
12
Table 11.1: Number of river in Malaysia (Source: Department of Irrigation and
Drainage, https://www.water.gov.my/index.php/pages/view/702)
Region Number of river
Peninsular Malaysia 89
Sabah 78
Sarawak 22
Total rivers 189
From the National Register River in 2017, Table 10.1 shows the total number of
rivers in Malaysia; 89 rivers in Peninsular Malaysia, 78 rivers in Sabah and 22 rivers
in Sarawak, respectively. Malaysian’s river becomes the hub of life for economic and
social activity whereby since the independence in 1957, Malaysia has experience
transformation from rural economy that based on agriculture and tin mining, into an
unprecedented rapid urbanization and industrialization (Chan et al., 2003). The
rubber estate has shifted to oil palm and the extensive tract of land was done by
Federal Land Development Agency (FELDA). This is followed by uncontrolled
logging as well expansion of commercial and industries. The impact of the activities
has result the overstressed of river system whereby the river reached its threshold to
receive the pollutants.
Malaysia is well known for its rich resources including water but ironically the water
is stressed (Chan, 2009). According to Tan Sri Razali (2001), it is due to the
mismanagement of water resource. It is concluded by Chan (2009) that generally the
development regarding water resource fails to underline the social aspect. Nowadays,
Malaysia has the River Basin Management as one of the divisions in Department of
Irrigation and Drainage that ensure the rivers in Malaysia are clean, vibrant and
liveable. According to the Lembaga Urus Air Selangor (2017), the main concept
applied by Department of Irrigation and Drainage is Integrated River Basin
Management (IRBM) includes the aspects of protection, conservation, and integrated
river basin management. In addition, the well-known approach toward river is River
13
of Life focuses on three components namely river cleaning, river master planning
and beautification, and river development. The approach is through the civic science
which is awareness, knowledge, skill and action; that associated with the community
resilience. It is integrated with the objectives of River of Life that also target to
promote sense of ownership toward the river in achieving long term sustainable
behavior to appreciate the river development.
11.1.4 Summary of River Development
Table 11.2: Summary of river development
River development
River profile Challenges Rivers in Malaysia
Character
Evolution
Behaviour
Maintaining natural
state, multiple roles,
complexity, uncertainty,
and sustainability
Issue: Resource fails to
underline the social
aspect (Chan, 2009)
The Table 11.2 shows the summary of river development. It is important to
understand the river profile and challenges in developing a river in urban
neighborhood. This is because disturbances from anthropogenic activities influence
the river development and create some challenges in achieving sustainability. In
context of Malaysia, this research investigates the rivers in Malaysia to understand
the status of river development in urban neighborhood.
11.2 Community resilience (overview)
Community resilience comes in many definitions according to its context. The initial
definition of resilience was introduced by Holling (1973) whereby he relates it with
ecological resilience on how the ecosystem responded to the disturbance by man.
This mean the ecological resilience is explained through evolutionary change. The
resilience itself means to leap back, rebound or recoil which emphasize on processes
rather than the ability to reach the climax (Folke, 2006). In context of social
14
resilience, community resilience is a subset of social resilience and is defined as the
existence, development, and engagement of community resources by community
members to thrive in an environment characterized by change, uncertainty,
unpredictability, and surprise (Magis, 2010). Community resilience play vital role in
strengthening the strategic planning toward sustainable urban development as it
comes with many perspectives such as community resilience in public health and
crisis management (Ahmed et al., 2004), community resilience in natural resources,
community resilience in social science and many more (Magis, 2010). This studies
shows resilience is a must for urban to develop sustainably.
The role of community resilience in urban is to ensure the community able to
respond with the changes (Ahmed et al. (2004); Gibbon, Labonté, and Laverack
(2002)). Folke, Colding, and Fikret (2003) emphasizes that the change is inevitable
and need to be accepted by the community as well able to adapt with the uncertainty
and surprise. Community resilience create robustness in society by establishing the
capacity to absorb the disturbance to maintain function, structure and identity
(Anderies, Janssen, and Ostrom (2004); Walker, Holling, Carpenter, and Kinzig
(2004)). From these studies, it show that the role community resilience is important
in shaping a community that able to undergo uncertainty and changes as well respond
to it through their adaptation.
Aforementioned, community resilience a subset of social resilience as defined by
Adger (2000); the ability of a group or communities to cope with external stresses
and disturbances caused by the social, political and environmental change. In
addition, Folke (2006) defined social resilience as the necessity of human system to
learn in managing the changes which involves uncertainty and surprise as part of the
system process. The similarity between the two definitions is on the managing the
disturbance caused by uncertainty and surprises from social, political and
environment. It is needed to ensure the community able to adapt in urban stress and
live sustainably with unexpected change. Resilience itself can be measured by how
far the system can tolerate and yet maintain the system function (Wilson, 2012).
According to Wilson (2012), the quality of resilience can be measured through the
indicators such as resilience and vulnerability. As mentioned, these indicators will be
influenced by the drivers such as adaptive capacity (Folke et al., 2003), the capitals
15
(Magis, 2010); transition theory (Wilson, 2014), and stewardship (Hunter, 2011).
11.2.3 Indicators
Indicators are used to measure the community resilience. According to Wilson
(2012), the measurement is in range between resilient and vulnerable; whereby
resilient is to be considered as strong resilience while venerable is considered to be
weak resilience.
Figure 11.1: General measurement of community resilience (Source: Adapted from
(Wilson, 2012).
Figure 11.1 shows the general measurement of community resilience that applied in
the drivers. In resilient situation, the community is said to have improved access to
education, markets and skills. The modernization, technology advance and
globalization are part of being resilient. However, it also may contribute to the
community vulnerability. In vulnerable situation, the community is highlighted by
Wilson (2012) to face the loss of environmental capital through destruction and
degradation, and social capital through such as outmigration. This indicator is
depending on the drivers because the drivers play role in shaping the community
resilience.
Resilient (strong) … Vulnerable (weak)
16
11.2.4 Summary of community resilience
Table 11.3: Summary of community resilience
Community resilience
Definition Driver Indicators
Capacity to adapt with
the change (Magis, 2010)
- Adaptive
capacity
- Capitals
(Social,
environmental,
economy)
- Transition
theory
- Stewardship Influ
en
ce
d d
rive
rs t
hro
ug
h S
oc
ial
me
mo
ry a
nd
Pa
th d
ep
en
de
nc
y
Resilient (strong)…
Vulnerable (weak)
The Table 11.3 shows the summary of community resilience. It is important to
understand the definition of community resilience as there are many definitions from
many aspects but interrelated with one another. Community resilience is influence by
the driver and the drivers are influenced by the social memory and path dependency
that can be results the measurement; either resilient or vulnerable.
11.3 Cultural Ecosystem Services
Cultural Ecosystem Services (CES) is one of the services in Ecosystem Services
(ESS). Ecosystem Services is the direct and indirect services whereby human can
gain benefits from the ecosystem (Austin, 2014). According to The Economics of
Ecosystems & Biodiversity (TEEB), there are four major are services within
ecosystem services namely Provisioning Services, Regulating Services, Habitat or
Supporting Services, and Cultural Services. Firstly, the Provisioning Services
describe the material or energy outputs from ecosystem that includes food, raw
materials, fresh water and medicinal resources. For example in food aspect, the
ecosystems provide the conditions for growing food that to sustain the humanity.
17
Secondly, the Regulating Services are the services that ecosystems provide by acting
as regulators. For example, Regulating Services can be seen through the regulation of
the air and soil quality, or flood food provision and disease control. Thirdly, the
Supporting Services complement the other services. For example, the Supporting
Service includes the nutrient cycling that maintains the conditions for life on Earth
and habitats that provided for the species to survive. Lastly, the Cultural Ecosystem
Services is the intangible value the community benefit from such as recreation,
mental and physical health, tourism, aesthetic, and many more.
According Hassan et al. (2005) and The Economics of Ecosystems & Biodiversity
(TEEB), Cultural Ecosystem Services is commonly defined as the ‘nonmaterial
benefits people obtain from ecosystems through spiritual enrichment, cognitive
development, reflection, recreation, an aesthetic experience, including knowledge
systems, social relations, and aesthetic’. Cultural Ecosystem Services is more directly
experienced and can be appreciated through intuition by community (Abson et al.,
2017). However, due to its intangible dimension (Haase et al. (2014); Vollmer et al.
(2015), it is highlighted that of all Ecosystem Services, Cultural Ecosystem Services
are the least explored in literature review. According to La Rosa, Spyra, and
Inostroza (2016), Cultural Ecosystem Services receives little attention especially
regarding the relevant benefit that community and the urban planning processes may
gained from Cultural Ecosystem Services.
In relation to the river development, the urban river has the potential to be developed
as a park (Plieninger et al., 2015) and become part of communal space which is to
Cultural Ecosystem Services, park is valued highly for its landscape characteristic
(Austin, 2014). River development is potential in providing the aesthetical value,
sense of place, recreational, inspirational value and educational value (La Rosa et al.,
2016) that addressed in shaping the community resilience in urban neighbourhood.
Thus, the visual attraction may be seen in river development that is shaped by the
community resilience.
18
11.3.1 Function of Cultural Ecosystem Services
Aesthetic is referring to the visual quality gained by human whereas spiritual is
referring to the experience through senses that can be interpreted and appreciated
with our mind. Study by Austin (2014) shows that people responds to landscape
characteristics such as the texture, pattern, colour, sense of harmony, and many more.
According to The Economic of Ecosystem and Biodiversity (TEEB), the aesthetic
contribute to appreciation value as well becoming inspiration in culture, art and
design of language, knowledge and natural environment as these has been related
intimately with human since history and nowadays has growing in becoming source
of inspiration in science. Meanwhile, the spiritual is associated with the nature
setting that form the sense of belonging.
Health and recreation are combined together and interpreted as the landscape that
consist of spaces for physical activities (Austin, 2014). According to The Economic
of Ecosystem and Biodiversity (TEEB), through such activities, it improves
community’s well-being by giving sense of relaxation to them. This proves and been
increasingly recognized that green spaces play role in maintaining community’s
mental and physical health despite of the difficulties in measuring it. Indirectly, this
situation gives impact on economic value because from the economic perspective,
the value of open space and recreation in urban area was not fully understood and yet
physical and psychological health become one of the concerns in urban (Austin,
2014). Study by Grant (2010) proves that open spaces and health is strongly related
whereby people in area with high mass of greenery are three times more active and
40% experience less obese.
Large portion of nature becomes the main attraction in tourism whereby Austin
(2014) state that the tourist’s journey consist of part which dedicated to travel and
visit park with high quality and recreational facilities. In relation to high quality of
park, it has been studied that due to the existence of park, the property tax increases.
For example, the sales tax for residential is higher with the existing of park in the
neighbourhood compared to residential without park; in a way, the existing of park
reduce the cost for stormwater management whereby it regulates the nature process
naturally (Austin, 2014). In reference to The Economic of Ecosystem and
19
Biodiversity (TEEB), this shows that tourism contributes to economic benefits which
become one of the income sources for many countries.
11.3.2 Factor of Cultural Ecosystem Services
The factor that affect Cultural Ecosystem Services is divided into two categories
namely economic value and sustaining ecosystem services (Austin, 2014) as Cultural
Ecosystem Services is valued differently by different people’s perspective under
different socio-economic condition (Plieninger et al., 2015). According to Throsby
(2001), Cheng (2006), Bucci and Segre (2011), the economic concept has taken
shape to assess the Cultural Ecosystem Services because out of all indicators in
Ecosystem Services Assessment, only 6% is referred to Cultural Ecosystem Services.
According Austin (2014), economic value is one of the vital factors that support and
at the same time diminished the Cultural Ecosystem Services by the land use.
Traditionally, only commercial and industrial has been understood to add the
economic value of a city. Nowadays, ecosystem plays part both directly and
indirectly influencing the economic value whereby ecosystem indirectly reduce the
maintenance cost of system which in turn helps the economic value (Austin, 2014).
The Cultural Ecosystem Services is also depending on the health of Ecosystem
Services; on how the health of ecosystem is being taken care of. It refers on the
human access to manage the ecosystem and it respond by influencing the community
experience in nature, the cultural understanding, and the education opportunity
(Austin, 2014). In regards to community experience in nature, Austin (2014)
highlights the health and aesthetic value whereby these two aspect gives the
enjoyment in nature. As mentioned in The Economic of Ecosystem and Biodiversity
(TEEB), the nature environment is one of the common elements that create sense of
belonging within community. This can be seen as one of the links between
community resilience and Cultural Ecosystem Services whereby the ecosystem affect
the community’s awareness and perception to the environment. According to Daily
(1997), it is the community that has been sustained by nature world and not the other
way around because the nature is the main resource that provide continuous product
for human to survive (Wilson, 2012). Therefore, the functions provided by Cultural
20
Ecosystem Services need to be distributed throughout community to gain and
experience the benefits.
11.3.3 Summary of Cultural Ecosystem Services
Table 11.4: Summary of Cultural Ecosystem Services
Cultural Ecosystem Services
Definition Function/ benefit/ services
Non-material benefit
through spiritual enrichment,
cognitive development,
reflection, recreation, an
aesthetic experience
Aesthetic
& spiritual
Health &
recreation Education Tourism
Factors
Economic value Sustaining Ecosystem Services
The Table 11.4 shows the summary of Cultural Ecosystem Services. It is important
to understand the definition in order to explain the function of Ecosystem Services.
The factors are economic value and sustaining Ecosystem Services that influence the
functions stated in Table 11.4.
11.4 Relationship between community resilience and Cultural Ecosystem
Services within river development
According to Wilson (2012), the community resilience is glued together by
environmental, social and economy capital. It is further explained that the urban
environment itself affects the community resilience by influencing the consumption
behaviour (Zhan Wang, Deng, Wong, Li, & Chen, 2018). The river development is
seen as part of the urban environment too and consumption behaviour is referring to
the community in urban area. Aforementioned, the increase of demand has cause the
land use pattern change. The increase land use pattern and changes lead is influenced
by Cultural Ecosystem Service (Plieninger et al., 2015) and degradation in the river
development has result the imbalance development and retard the sustainability
21
strategies. This shows the negative impact on the community and environment is due
to anthropogenic activities which initiated by human themselves.
Figure 11.2: Theoretical framework of research
The overall denominator of the research is river development that shaped by
community resilience. Community resilience is influence by the drivers; which is
influenced by the factors. Thus, the factors develop the community’s knowledge
(Berkes et al. (2003); Gunderson et al. (2002)),create awareness (Hunter, 2011),
slowly formulate their perception (Gregory, 2006) toward river development, and
determine their acceptation (Cha et al. (2011). Finally, it forms their stewardship
(Ahmed et al., 2004) of the community that shapes their resiliency toward river
development. Based on the Figure 11.2, this research focuses the river development
shaped by community resilience through Cultural Ecosystem Services. Thus, through
Cultural Ecosystem Services, it improves the river development in the perspective of
landscape architecture.
22
12. Research methodology
This research is to investigate on how the community resilience shapes river
development through Cultural Ecosystem Services in urban neighbourhood, therefore
it involves three methods namely observation, interview and semi structured
questionnaires, and Driver-Force-Pressure-State-Impact-Response (DPSIR)
Framework.
12.1 Observation
The observation is to recognize the river profile that affect the community resilience
through Cultural Ecosystem Services. It is to achieve objective one and two of
research; to identify the factors and level of community resilience. The data
collection will be based on the evolution of river from 1957 which will be collected
from Department of Irrigation and Drainage, Department of Environment,
Department of Landscape in Dewan Bandaraya Kota Kinabalu and other Non-
Government Organization that has involved in Sembulan River Park. The data will
be using Google Maps or ArcGis to analyse the changes from 1957 up until now.
Field observation will also be involved to confirm the current status of the river.
According to Chan et al. (2003), the issues that contribute to rivers begins after the
independence whereby the rapid development of agriculture and followed by
industrialization. Thus, it overstressed the river system as many rivers have reached
its limit. The health of river can be observed through water quality (Bunn et al.,
2010) as the ecological status of river.
12.2 Interview and Semi-Structured Questionnaire
Interview and semi-structured questionnaire are to achieve the objective one and two;
understand the factors and level of community resilience among the community
nearby Sembulan River Park, Kota Kinabalu. The data collection will be based on
the residences (including squatters) nearby the riverside and expertise from local
authorities. The questionnaire will be based on enquiry of their knowledge of river
23
development, followed by their awareness that formulate their perception and
acceptance to the current river development in urban area. NVIVO will be used to
analyse the data. In the end, stewardship can be explained through the sequences of
knowledge, awareness, perception and acceptance. Thus, this indicates the level of
community resilience on the study area.
12.3 Drivers-Pressure-State-Impact-Response (DPSIR) Framework
Drivers-Pressure-State-Impact-Response Framework is one of tools that measure the
cause and impact relationship (Chiang, 2018). This is to achieve the last objectives;
to determine the effect of Cultural Ecosystem Services toward community resilience
within river development in urban neighbourhood. Some studies use it to assess the
knowledge, skills and network capacity achieved from different disturbances (Ling &
Chiang, 2018). Thus, it is useful to describe the relationship between community
resilience through Cultural Ecosystem Services on river development in urban
neighbourhood as entity in this research.
24
Figure 12.1: DPSIR framework
According to the Figure 12.1, the DPSIR framework is divided into five attributes.
Firstly is the Driver which is a need that cause result the issues or disturbance. In
regards to this research, the Driver questions “What are the issues?” Secondly is the
Pressure; it is associated with the cause of issue. It questions “What cause the
issues?” Thirdly is the State which is questions “What is the impact of the issue?”
Fourthly is the Impact; that helps in determining the quality of ecosystem and
welfare of human beings. It questions “What/whom the impact goes to?” And lastly
is the Response; it is a result of undesired impact and can affect any parts of the
framework. It questions “What action has been taken to tackle the issue?”
25
12.4 Summary of Methodology
R. Objectives Methodology Data source Variables Tools to analyze
(a) To identify factors of community
resilience in urban neighborhood
that shapes river development
through Cultural Ecosystem Services.
Interview and semi
structured
questionnaire
River urban user
(including
squatter)
Knowledge,
awareness,
perception,
acceptance,
stewardship
NVIVO
(b) To examine the level of
community resilience toward river
development through Cultural
Services in urban neighborhood.
River profile Sembulan River
Park
Evolution of
river, riparian
health, water
quality
Google Maps or
ArcGis
(c) To determine the effect of
Cultural Ecosystem Services toward
community resilience within river
development in urban
neighborhood.
Driver force -
Pressure - State -
Impact - Response
(DPSIR) Framework:
Describe the
interaction
between society
and environment
River urban user
(including
squatter) and
Sembulan River
Park
Knowledge,
awareness,
perception,
acceptance,
stewardship +
Evolution of
river, riparian
health, water
quality
DPSIR Framework
26
13. Flow chart
27
14. Anticipated findings
Rapid urbanization in river development influenced by community resilience through
Cultural Ecosystem Services. Therefore, this research anticipating that:
i. The river development shaped by community resilience through Cultural
Ecosystem Services is influence by the knowledge, awareness,
perception, acceptance and stewardship of community nearby the river.
ii. The community resilience within river development is affected through
aesthetic that form the visual attractiveness for the community to
appreciate the river development.
15. Contribution
This research is to produce a framework on how the future river development able to
be sustained by the community resilience through Cultural Ecosystem Services. It
contributes to the concept of Integrated River Basin Management (IRBM) applied by
Department of Irrigation and Drainage that highlights on protection, conservation
and integrated river basin management. It is also parallel with River of Life approach
to a vibrant and livable urban river for community.
28
16. Gantt chart and Milestones
Figure 16.1: Gantt Chart
29
Figure 16.2: Milestones
30
17. References
Abson, D. J., Fischer, J., Leventon, J., Newig, J., Schomerus, T., Vilsmaier, U., . . .
Lang, D. J. (2017). Leverage points for sustainability transformation. AMBIO,
46(1), 30-39. doi: 10.1007/s13280-016-0800-y
Adger, W. N. (2000). Social and ecological resilience: are they related? Progress in
Human Geography, 24(3), 347-364. doi: 10.1191/030913200701540465
Ahmed, R., Seedat, M., Niekerk, A. v., & Bulbulia, S. (2004). Discerning
Community Resilience in Disadvantaged Communities in the Context of
Violence and Injury Prevention. South African Journal of Psychology, 34(3),
386-408. doi: 10.1177/008124630403400304
Anderies, J. M., Janssen, M. A., & Ostrom, E. (2004). A Framework to Analyze the
Robustness of Social-ecological Systems from an Institutional Perspective.
Ecology and Society, 9(1). doi: 10.5751/ES-00610-090118
Asakawa, S., Yoshida, K., & Yabe, K. (2004). Perceptions of urban stream corridors
within the greenway system of Sapporo, Japan. Landscape and Urban
Planning, 68(2), 167-182. doi: https://doi.org/10.1016/S0169-
2046(03)00158-0
Austin, G. (2014). Green Infrastructure for Landscape Planning: Integrating Human
and Natural Systems: Taylor & Francis.
Baschak, L., & Brown, R. (1994). River systems and landscape networks. Landscape
planning and ecological networks, 6, 179.
Berkes, F., Colding, J., & Folke, C. (2003). Navigating social-ecological systems:
Building resilience for complexity and change. Cambridge, UK: Cambridge
University Press.
Blignaut, J., Wit, M. d., & Zy, H. v. (2011). TEEB Manual for Cities: Ecosystem
Services in Urban Management.
Brierley, G., Fryirs, K., Outhet, D., & Massey, C. (2002). Application of the River
Styles framework as a basis for river management in New South Wales,
Australia. Applied Geography, 22(1), 91-122. doi:
https://doi.org/10.1016/S0143-6228(01)00016-9
31
Brotons, J. C., & Mallari, J. (2016). How to Revive an Ailing River. Retrieved
08/04, 2018, from https://development.asia/case-study/how-revive-ailing-
river
Cha, Y. J., Shim, M.-P., & Kim, S. K. (2011). The Four Major Rivers Restoration
Project. from
un.org/waterforlifedecade/green...2011/.../session_8_water_planning_cases_k
orea.pdf
Chan, N. W. (2009). Issues and challenges in water governance in Malaysia (Vol.
6).
Chan, N. W., Abdullah, A. L., Ibrahim, A. L., & Ghazali, S. (2003). River pollution
and restoration towards sustainable water resources management in
Malaysia. Paper presented at the Society, Space & Environment in a
Globalised World: Challenges and Prospects, Penang, Malaysia.
Chen, W. Y., Hua, J., Liekens, I., & Broekx, S. (2018). Preference heterogeneity and
scale heterogeneity in urban river restoration: A comparative study between
Brussels and Guangzhou using discrete choice experiments. Landscape and
Urban Planning, 173, 9-22. doi:
https://doi.org/10.1016/j.landurbplan.2018.01.010
Chiang, Y.-C. (2018). Exploring community risk perceptions of climate change - A
case study of a flood-prone urban area of Taiwan. Cities, 74, 42-51. doi:
https://doi.org/10.1016/j.cities.2017.11.001
Cortinovis, C., & Geneletti, D. (2018). Ecosystem services in urban plans: What is
there, and what is still needed for better decisions. Land Use Policy, 70, 298-
312. doi: https://doi.org/10.1016/j.landusepol.2017.10.017
Costello, D., Johns, M., & Guilfoyle, A. (2007). Understanding & Building
Resilience in the South West. Paper presented at the Australian Social
Conference.
Cutter, S. L., Barnes, L., Berry, M., Burton, C., Evans, E., Tate, E., & Webb, J.
(2008). A place-based model for understanding community resilience to
natural disasters. Global Environmental Change, 18(4), 598-606. doi:
https://doi.org/10.1016/j.gloenvcha.2008.07.013
Darby, S., & Sear, D. (2008). River Restoration: Managing the Uncertainty in
Restoring Physical Habitat: John Wiley & Sons, Ltd.
Davis, R., Cook, D., & Cohen, L. (2005). A Community Resilience Approach to
Reducing Ethnic and Racial Disparities in Health. American Journal of
Public Health, 95(12), 2168-2173. doi: 10.2105/AJPH.2004.050146
32
Deng, X., & Xu, Y. (2018). Degrading flood regulation function of river systems in
the urbanization process. Science of The Total Environment, 622-623, 1379-
1390. doi: https://doi.org/10.1016/j.scitotenv.2017.12.088
Eric, Y. L. T. (2018). In R. M. Fridaus (Ed.).
Everard, M., & Moggridge, H. L. (2012). Rediscovering the value of urban rivers.
Urban Ecosystems, 15(2), 293-314. doi: 10.1007/s11252-011-0174-7
Eze, P. N., & Knight, J. (2018). A geomorphological characterisation of river
systems in South Africa: A case study of the Sabie River. Physics and
Chemistry of the Earth, Parts A/B/C. doi:
https://doi.org/10.1016/j.pce.2018.01.001
Folke, C. (2006). Resilience: The emergence of a perspective for social–ecological
systems analyses. Global Environmental Change, 16(3), 253-267. doi:
https://doi.org/10.1016/j.gloenvcha.2006.04.002
Folke, C., Colding, J., & Fikret, B. (2003). Synthesis: Building Resilience and
Adaptive Capacity in Social- Ecological Systems Navigating Social-
Ecological Systems: Building Resilience for Complexity and Change. New
York: Cambridge University Press.
Furuta, N., & Shimatani, Y. (2017). Integrating ecological perspectives into
engineering practices – Perspectives and lessons from Japan. International
Journal of Disaster Risk Reduction. doi:
https://doi.org/10.1016/j.ijdrr.2017.12.003
Gibbon, M., Labonté, R., & Laverack, G. (2002). Evaluating community capacity.
Health Soc Care Community (Vol. 10).
González del Tánago, M., García de Jalón, D., & Román, M. (2012). River
Restoration in Spain: Theoretical and Practical Approach in the Context of
the European Water Framework Directive. Environmental Management,
50(1), 123-139. doi: 10.1007/s00267-012-9862-1
Grant, L. (2010). Multi-Functional Urban Green Infrastructure (pp. 47).
Gregory, K. J. (2006). The human role in changing river channels. Geomorphology,
79(3), 172-191. doi: https://doi.org/10.1016/j.geomorph.2006.06.018
Gunderson, L. H., Pritchard, L., & Environment, I. C. o. S. U. S. C. o. P. o. t. (2002).
Resilience and the Behavior of Large-Scale Systems: Island Press.
Haase, D., Larondelle, N., Andersson, E., Artmann, M., Borgström, S., Breuste, J., . .
. Elmqvist, T. (2014). A Quantitative Review of Urban Ecosystem Service
33
Assessments: Concepts, Models, and Implementation. AMBIO, 43(4), 413-
433. doi: 10.1007/s13280-014-0504-0
Hassan, R. M., Scholes, R., Ash, N., Condition, M. E. A., & Group, T. W. (2005).
Ecosystems and Human Well-Being: Current State and Trends: Findings of
the Condition and Trends Working Group: Island Press.
Holling, C. S. (1973). Resilience and Stability of Ecological Systems. Annual Review
of Ecology and Systematics, 4(1), 1-23. doi:
10.1146/annurev.es.04.110173.000245
Hunter, M. R. (2011). Impact of ecological disturbance on awareness of urban nature
and sense of environmental stewardship in residential neighborhoods.
Landscape and Urban Planning, 101(2), 131-138. doi:
https://doi.org/10.1016/j.landurbplan.2011.02.005
Johnson, E. S., Bell, K. P., & Leahy, J. E. (2018). Disamenity to amenity: Spatial and
temporal patterns of social response to river restoration progress. Landscape
and Urban Planning, 169, 208-219. doi:
https://doi.org/10.1016/j.landurbplan.2017.09.008
Junker, B., & Buchecker, M. (2008). Aesthetic preferences versus ecological
objectives in river restorations. Landscape and Urban Planning, 85(3), 141-
154. doi: https://doi.org/10.1016/j.landurbplan.2007.11.002
Kasnoon, K. (2003). 5 sungai dikenal pasti paling tercemar di negara ini. Retrieved
28/04, 2018, from http://www.astroawani.com/berita-awani745/5-sungai-
dikenal-pasti-paling-tercemar-di-negara-ini-23535
Kondolf, G. M., & Pinto, P. J. (2017). The social connectivity of urban rivers.
Geomorphology, 277, 182-196. doi:
https://doi.org/10.1016/j.geomorph.2016.09.028
Kumar, P., Masago, Y., Mishra, B. K., & Fukushi, K. (2018). Evaluating future
stress due to combined effect of climate change and rapid urbanization for
Pasig-Marikina River, Manila. Groundwater for Sustainable Development, 6,
227-234. doi: https://doi.org/10.1016/j.gsd.2018.01.004
La Rosa, D., Spyra, M., & Inostroza, L. (2016). Indicators of Cultural Ecosystem
Services for urban planning: A review. Ecological Indicators, 61, 74-89. doi:
https://doi.org/10.1016/j.ecolind.2015.04.028
Lah, T. J., Park, Y., & Cho, Y. J. (2015). The Four Major Rivers Restoration Project
of South Korea:An Assessment of Its Process, Program, and Political
Dimensions. The Journal of Environment & Development, 24(4), 375-394.
doi: 10.1177/1070496515598611
34
. Laporan Tahunan JPS 2016. (2016).
Latip, N. S. A., Shamsudin, S., & Liew, M. S. (2012). Functional Dimension at
‘Kuala Lumpur Waterfront’. Procedia - Social and Behavioral Sciences, 49,
147-155. doi: https://doi.org/10.1016/j.sbspro.2012.07.013
Lerch, D. (2015). Six Foundations for Building Community Resilience.
Liao, K. H. (2013). Singapore's active, beautiful clean waters.
Ling, T.-Y., & Chiang, Y.-C. (2018). Strengthening the resilience of urban retailers
towards flood risks - A case study in the riverbank region of Kaohsiung City.
International Journal of Disaster Risk Reduction, 27, 541-555. doi:
https://doi.org/10.1016/j.ijdrr.2017.11.020
Liu, J., Shen, Z., Yan, T., & Yang, Y. (2018). Source identification and impact of
landscape pattern on riverine nitrogen pollution in a typical urbanized
watershed, Beijing, China. Science of The Total Environment, 628-629, 1296-
1307. doi: https://doi.org/10.1016/j.scitotenv.2018.02.161
Magis, K. (2010). Community Resilience: An Indicator of Social Sustainability.
Society & Natural Resources, 23(5), 401-416. doi:
10.1080/08941920903305674
Masud, M. M. A., Moni, N. N., Azadi, H., & Van Passel, S. (2018). Sustainability
impacts of tidal river management: Towards a conceptual framework.
Ecological Indicators, 85, 451-467. doi:
https://doi.org/10.1016/j.ecolind.2017.10.022
Md. Yassin, A., Eves, C., & McDonagh, J. (2010). An evolution of waterfront
development in Malaysia.
Palmer, M. A., & Filoso, S. (2009). Restoration of Ecosystem Services for
Environmental Markets. Science, 325(5940), 575-576. doi:
10.1126/science.1172976
Palmer, M. A., Hondula, K. L., & Koch, B. J. (2014). Ecological Restoration of
Streams and Rivers: Shifting Strategies and Shifting Goals. Annual Review of
Ecology, Evolution, and Systematics, 45(1), 247-269. doi: 10.1146/annurev-
ecolsys-120213-091935
Patel, R. B., & Gleason, K. M. (2018). The association between social cohesion and
community resilience in two urban slums of Port au Prince, Haiti.
International Journal of Disaster Risk Reduction, 27, 161-167. doi:
https://doi.org/10.1016/j.ijdrr.2017.10.003
35
Pelling, M. (2003). The Vulnerability of Cities: Natural Disasters and Social
Resilience: Earthscan Publications.
Plieninger, T., Bieling, C., Fagerholm, N., Byg, A., Hartel, T., Hurley, P., . . .
Huntsinger, L. (2015). The role of cultural ecosystem services in landscape
management and planning. Current Opinion in Environmental Sustainability,
14, 28-33. doi: https://doi.org/10.1016/j.cosust.2015.02.006
Prominski, M., Stokman, A., & Zeller, S. (2012). River, Space, Design: Planning
Strategies, Methods and Projects for Urban Rivers: Birkhauser.
Saxton, N. (2013). River restoration in a subtropical region: A case study in South-
East.
Schipper, E. L. F., & Langston, L. (2015). A comparative overview of resilience
measurement frameworks: Working Paper 422. London, United Kingdom:
Overseas Development Institute.
Solins, J. P., Thorne, J. H., & Cadenasso, M. L. (2018). Riparian canopy expansion
in an urban landscape: Multiple drivers of vegetation change along headwater
streams near Sacramento, California. Landscape and Urban Planning, 172,
37-46. doi: https://doi.org/10.1016/j.landurbplan.2017.12.005
Southon, G. E., Jorgensen, A., Dunnett, N., Hoyle, H., & Evans, K. L. (2018).
Perceived species-richness in urban green spaces: Cues, accuracy and well-
being impacts. Landscape and Urban Planning, 172, 1-10. doi:
10.10164/j.andurbplan.2017.12.002
Speed, R. A., Li, Y., Tickner, D., Huang, H., Naiman, R. J., Cao, J., . . . Wei, Y.
(2016). A framework for strategic river restoration in China. Water
International, 41(7), 998-1015. doi: 10.1080/02508060.2016.1247311
Steward, A. L., Negus, P., Marshall, J. C., Clifford, S. E., & Dent, C. (2018).
Assessing the ecological health of rivers when they are dry. Ecological
Indicators, 85, 537-547. doi: https://doi.org/10.1016/j.ecolind.2017.10.053
van den Brandeler, F., Gupta, J., & Hordijk, M. (2018). Megacities and rivers: Scalar
mismatches between urban water management and river basin management.
Journal of Hydrology. doi: https://doi.org/10.1016/j.jhydrol.2018.01.001
Vollmer, D., Prescott, M. F., Padawangi, R., Girot, C., & Grêt-Regamey, A. (2015).
Understanding the value of urban riparian corridors: Considerations in
planning for cultural services along an Indonesian river. Landscape and
Urban Planning, 138, 144-154. doi:
https://doi.org/10.1016/j.landurbplan.2015.02.011
36
Walker, B., Holling, C. S., Carpenter, S. R., & Kinzig, A. P. (2004). Resilience,
Adaptability and Transformability in Social–ecological Systems. Ecology and
Society, 9(2). doi: 10.5751/ES-00650-090205
Wang, Z. (2018). Evolving landscape-urbanization relationships in contemporary
China. Landscape and Urban Planning, 171, 30-41. doi:
https://doi.org/10.1016/j.landurbplan.2017.11.010
Wang, Z., Deng, X., Wong, C., Li, Z., & Chen, J. (2018). Learning Urban Resilience
from a Social-Economic-Ecological System Perspective: a case study of
Beijing from 1978-2015. Journal of Cleaner Production. doi:
https://doi.org/10.1016/j.jclepro.2018.02.128
Weil, K. K., Cronan, C. S., Meyer, S. R., Lilieholm, R. J., Danielson, T. J.,
Tsomides, L., & Owen, D. (2018). Predicting stream vulnerability to
urbanization stress with Bayesian network models. Landscape and Urban
Planning, 170, 138-149. doi:
https://doi.org/10.1016/j.landurbplan.2017.11.001
Western, J., Stimson, R., Baum, S., & Van Gellecum, Y. (2005). Measuring
community strength and social capital. Regional Studies, 39(8), 1095-1109.
doi: 10.1080/00343400500328222
Wilson, G. A. (2012). Community Resilience and Environmental Transitions:
Routledge.
Wilson, G. A. (2014). Community resilience: path dependency, lock-in effects and
transitional ruptures. Journal of Environmental Planning and Management,
57(1), 1-26. doi: 10.1080/09640568.2012.741519