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Lessons from New York High Line Green Roof: Conserving Biodiversity and Reconnecting with Nature

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Abstract

The concept of sustainable urban design has appeared in different perspectives to minimize and reduce the negative impacts of urban expansion in terms of climatic and environmental drawbacks. One of the undeniable approaches of sustainable urban design is the adoption of green urban roofs. Green roofs are seen to have a substantial role in addressing and resolving environmental issues in the context of climate change. Research investigations have indicated that green roofs have a remarkable impact on decreasing rainwater runoff, reducing the heat island effect in urban spaces, and increasing biodiversity. Nevertheless, green roofs in urban spaces as a competent alternative to nature remains a standing question. To what extent can green roofs mimic the biodiversity that is seen in nature? Moreover, to what level is this approach practical for achieving a tangible reconnection with nature, or so-called biophilia? This study attempts to discuss the essence and impact of green roofs in urban spaces based on a case study approach. The study reflected lessons from the New York High Line Green Roof regarding biophilia and biodiversity in this case study. It concludes with key lessons that can be transferred to other urban spaces with similar settings.
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Citation: Salih, K.; Saeed, Z.O.;
Almukhtar, A. Lessons from New
York High Line Green Roof:
Conserving Biodiversity and
Reconnecting with Nature. Urban Sci.
2022,6, 2. https://doi.org/
10.3390/urbansci6010002
Academic Editors:
Raúl Romero-Calcerrada,
Javier Cabello,
Manuel Pacheco-Romero and
Koldo Trapaga Monchet
Received: 11 November 2021
Accepted: 24 December 2021
Published: 28 December 2021
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4.0/).
Case Report
Lessons from New York High Line Green Roof: Conserving
Biodiversity and Reconnecting with Nature
Kawar Salih 1, *, Zaid O. Saeed 2, * and Avar Almukhtar 3
1Research Center, Duhok Polytechnic University, Duhok 42001, Iraq
2School of Design and the Built Environment, Curtin University, Bentley, WA 6102, Australia
3School of the Built Environment, Oxford Brookes University, Oxford OX3 0BP, UK;
a.almukhtar@brookes.ac.uk
*Correspondence: kawar.salih@dpu.edu.krd (K.S.); z.alawadi@postgrad.curtin.edu.au or
zaidosama94cpm@gmail.com (Z.O.S.)
Abstract:
The concept of sustainable urban design has appeared in different perspectives to minimize
and reduce the negative impacts of urban expansion in terms of climatic and environmental draw-
backs. One of the undeniable approaches of sustainable urban design is the adoption of green urban
roofs. Green roofs are seen to have a substantial role in addressing and resolving environmental
issues in the context of climate change. Research investigations have indicated that green roofs have
a remarkable impact on decreasing rainwater runoff, reducing the heat island effect in urban spaces,
and increasing biodiversity. Nevertheless, green roofs in urban spaces as a competent alternative to
nature remains a standing question. To what extent can green roofs mimic the biodiversity that is seen
in nature? Moreover, to what level is this approach practical for achieving a tangible reconnection
with nature, or so-called biophilia? This study attempts to discuss the essence and impact of green
roofs in urban spaces based on a case study approach. The study reflected lessons from the New York
High Line Green Roof regarding biophilia and biodiversity in this case study. It concludes with key
lessons that can be transferred to other urban spaces with similar settings.
Keywords:
green roofs; biodiversity; biophilia; the high line; reconnection with nature; green urbanism
1. Introduction
Over the last several decades, climate change has become one of the major issues for
the contemporary world. Transforming thousands of square miles to urban grey spaces
has influenced the ecosystem, wildlife existence and nature in the urban areas [
1
]. In
2018, the amount of CO
2
emission reached 33.5 Gt, driven by urbanization factors such
as buildings, transportation, industry, electricity and heat generation [
2
]. Considerable
research has been conducted regarding the climate change phenomenon; yet, most of this
research is limited to the presentation of theoretical frameworks for conserving biodiversity
in urban spaces [
3
5
]. The idea of sustainable urban design has appeared in different
perspectives, all aiming to minimize and reduce the negative impacts of urban expansion
on the biodiversity of urban spaces. One of the key approaches of sustainable urban design
is the adoption of green urban roofs [68].
Green roofs are seen to have a substantial role in addressing and resolving environ-
mental issues in the context of climate change. For instance, research investigations have
indicated that green roofs have a significant impact on decreasing rainwater runoff, re-
ducing the heat island effect in urban spaces, and conserving the ecosystem [
9
,
10
]. Green
roofs are highly effective in reducing the carbon footprint and the heat island effect in
urban spaces [
11
13
]. Additionally, green roofs positively enhance urban air quality by
mitigating air pollution and purifying the urban atmosphere through their features and
characteristics [
14
16
]. Large-scale green roofs provide an interactive ecological setting that
is recognised as a source of relief for the urban scheme and a preserver of its biodiversity.
Urban Sci. 2022,6, 2. https://doi.org/10.3390/urbansci6010002 https://www.mdpi.com/journal/urbansci
Urban Sci. 2022,6, 2 2 of 13
Moreover, these roofs are seen as a replacement for the existence of wildlife within urban
contexts. Having such features in urban spaces not only preserves the natural biodiver-
sity of the ecological system; it is a substantial element for reconnecting human beings
with nature as well [
17
,
18
]. The human reconnection with nature has been addressed as
a challenging aspect in the urban context due to the complexity of achieving a tangible
connection as well as the nature of urban expansion, which tends towards building rather
than preserving. However, green urbanism in general is seen to be a promising alternative
for reconnecting the urban space with the nature while preserving eco-diversity within the
urban context [19,20].
Nevertheless, the adoption of green roofs in urban spaces as a competent alternative
for nature in the urban areas remains a standing question. To what extent can green roofs
mimic the biodiversity that is seen in nature? Moreover, to what level is this approach
practical for achieving a tangible reconnection with nature, so-called biophilia? Accordingly,
this study attempts to discuss the essence and impact of green roofs in urban spaces based
on a case study approach. The study will analyse the New York High Line Green Roof
regarding biophilia and biodiversity aspects in urban areas. The study will conclude with
key lessons that can be applied to other urban spaces with similar settings.
This paper takes a qualitative approach to discussing the concept of biophilia and
biodiversity in urban spaces from previous studies in Section 2, then links the two main
concepts to the application of green roofs in Section 3. Section 4provides background about
the High Line Green Roof, while Sections 5and 6reflect on the conceptual aspects of the
project through visual analysis of pictures as well as through previous data and references.
The study also derives key aspects learned from the High Line regarding the biodiversity
and biophilia achieved in this case. Lastly, Section 7concludes the study and suggests
further research into the scope of sustainability in urban spaces.
2. Biophilia, Biodiversity and Urban Spaces
2.1. Biophilia
Biophilia is a hypothesis that emerged in the late 20th century. Wilson defined biophilia
in 1984 as the preference and the pursuit of nature by humans, which is considered a
genetic root inherited millions of years ago when humans were highly associated with the
natural environment [
21
]. This old association might have influenced human behavior
toward nature, and it has remarkable effects on human health in general. Kellert (2008)
demonstrated that nature can significantly improve healing and recovery from illness,
social problems, motivation, physiological problems, and the human brain [
22
]. Research
associated with the impact of nature on the human species started with the beginning
of the biophilia concept. Old research as far back as 1984 suggested that patients with a
natural view can heal more quickly than those without [
23
]. Later research pointed out
that walking in nature improves self-esteem by 90% [
24
]. This indicates that the human
connection with nature has psychological benefits. This was deeply studied later on, and
many scholars noticed that this connection leads to numerous health benefits and better
quality of life [
22
]. Therefore, Beatley (2011) stressed that ‘we need nature in our lives; it
is not optional but essential’ [
25
]. Moreover, it has been mentioned that as the world is
becoming more urban, the human connection to nature is becoming more difficult [
25
].
Accordingly, human contact with nature is a basic need that should be reflected widely in
urban environments, which probably has been neglected or less-considered for many years.
The benefits of biophilia can be achieved in urban spaces if cities are designed based on
integrating nature into man-made environments. To adapt this Kellert, in 2011, suggested
biophilic design; this was then promoted and applied by Beatley and Newman in 2011
and 2014 respectively, which means it is not an old concept compared to other design con-
cepts [
22
,
25
,
26
]. Kellert and Calabrese (2015), in their Practice of Biophilic Design, suggested
fundamental rules for the effective practice of such design [
27
]. They highlighted that
biophilic design should sustain engagement with nature, encourage emotional attachment
to place and setting, and promote an expanded sense of relationship and responsibility for
Urban Sci. 2022,6, 2 3 of 13
both human and natural communities. This, in the end, requires integrated architectural
and urban solutions. Such ideas could be implemented, for example, through the fourteen
“patterns of biophilic design” [
28
]. These patterns are fundamentally categorised under the
headings of Nature in the Spaces, Natural Analogues, and Nature of the Space, as shown
in Figure 1[
28
]. Regarding Nature in the space, this approach emphasizes adding seven
design patterns that connect humans with nature through scenes or feelings from nature,
such as visual/non-visual connections, the presence of water, and the variability of nature
in terms of lighting, thermal and airflow. On the other hand, patterns regarding Natural
Analogues are added through biomorphic forms by using natural materials or mimicking
nature’s complexity and order. Biophilic design pattern can complexify to further ideas and
include Nature of the Space, such as the mystery of space, refuge, prospect, risk, and peril.
Urban Sci. 2022, 5, x FOR PEER REVIEW 3 of 14
in 2011 and 2014 respectively, which means it is not an old concept compared to other
design concepts [22,25,26]. Kellert and Calabrese (2015), in their Practice of Biophilic Design,
suggested fundamental rules for the effective practice of such design [27]. They
highlighted that biophilic design should sustain engagement with nature, encourage
emotional attachment to place and setting, and promote an expanded sense of relationship
and responsibility for both human and natural communities. This, in the end, requires
integrated architectural and urban solutions. Such ideas could be implemented, for
example, through the fourteen patterns of biophilic design” [28]. These patterns are
fundamentally categorised under the headings of Nature in the Spaces, Natural
Analogues, and Nature of the Space, as shown in Figure 1 [28]. Regarding Nature in the
space, this approach emphasizes adding seven design patterns that connect humans with
nature through scenes or feelings from nature, such as visual/non-visual connections, the
presence of water, and the variability of nature in terms of lighting, thermal and airflow.
On the other hand, patterns regarding Natural Analogues are added through biomorphic
forms by using natural materials or mimicking nature’s complexity and order. Biophilic
design pattern can complexify to further ideas and include Nature of the Space, such as
the mystery of space, refuge, prospect, risk, and peril.
Figure 1. 14 Patterns of Biophilic design. Data from source: [28].
Urbanization has not only affected the connection between nature and human beings;
it has affected the existence of wildlife features in urban areas, cities and living places as
well. Thus, urbanization has impacted the biodiversity of the ecological system in urban
spaces.
2.2. Biodiversity in Urban Spaces
Ecosystem and wildlife features are some of the significant environmental challenges
that urban design confronts when designing urban areas. The ecosystem refers to a unique
interaction between the living species and the physical environment that enables those
species to sustain their lifecycle and maintain balance in nature [29]. Accordingly, any
defect in the ecosystem will impact the lifecycle of living species [29]. On the other hand,
urbanization has been seen as an extensive threat when it comes to breaking the ecological
balance of the environment. Several studies [30–32] have clearly demonstrated the
negative impact of transforming natural green areas into grey urban developments where
the biodiversity of the ecosystem is adversely affected. Generally, urbanization has been
pictured as in contrast with biodiversity; where the former increases, the latter decreases
Figure 1. 14 Patterns of Biophilic design. Data from source: [28].
Urbanization has not only affected the connection between nature and human beings;
it has affected the existence of wildlife features in urban areas, cities and living places
as well. Thus, urbanization has impacted the biodiversity of the ecological system in
urban spaces.
2.2. Biodiversity in Urban Spaces
Ecosystem and wildlife features are some of the significant environmental challenges
that urban design confronts when designing urban areas. The ecosystem refers to a unique
interaction between the living species and the physical environment that enables those
species to sustain their lifecycle and maintain balance in nature [
29
]. Accordingly, any
defect in the ecosystem will impact the lifecycle of living species [
29
]. On the other hand,
urbanization has been seen as an extensive threat when it comes to breaking the ecological
balance of the environment. Several studies [
30
32
] have clearly demonstrated the negative
impact of transforming natural green areas into grey urban developments where the biodi-
versity of the ecosystem is adversely affected. Generally, urbanization has been pictured
as in contrast with biodiversity; where the former increases, the latter
decreases [3032]
.
Therefore, architects, urban planners, and decision-makers have been seeking practical and
innovative solutions that could preserve biodiversity in urban areas and lead to healthier
and sustainable urbanization. These urban solutions are a key aspect in planning and
designing urban areas while preserving the ecological diversity in these areas through a set
of features and practices.
Urban Sci. 2022,6, 2 4 of 13
3. Green Roofs in Urban Spaces
Green roofs, also referred to as “Planted Roofs,” “Living Roofs,” “Eco-roofs,” or “Gar-
den Roofs”, are roofs with vegetation on their final layers which are applied in urbanized
spaces [
33
]. They are classified as extensive, intensive, and semi-intensive based on their
depths [
34
]. Their depth starts with extensive types with a depth of less than 200 mm
of growing media and grows to semi-intensive and intensive with more than 200 mm of
growing substrate [
34
]. As the environmental outcomes of green roofs have been identified
in the existing literature, this study investigates the contribution of green roofs in linking
humans with nature and bio-diversification of the urbanized areas.
3.1. Green Roofs and Biophila
Green roofs can play a substantial role in reconnecting humans with nature. As
expanding urban areas translate to demolition of natural spaces, architects and urban
designers recommend increasing garden roofs to compensate for those natural views
removed by urban expansions. Biophilic Urbanism (BU) can be a solution when dense
cities fail to increase green land, and Green Infrastructure (GI) can be used as an alternative
approach including green walls, roofs, and balconies [
35
]. This is widely seen in Singapore,
which has founded the SkyRise Greening Initiative (SRGI) to assess the quality of planted
roofs in the early phases of building designs [
26
]. Therefore, green roofs are presented as
a considerable dimension of Biophilic Urbanism, or BU [
17
]. The governments of Japan,
Singapore, Belgium, and Germany highly encourage the use of green roofs in urban areas
because of these benefits [
36
]. Moreover, studies have noticed a relationship between
rooftop forests and psychological illness improvements in cities [
37
]. However, the studies
which have investigated the contribution of a green roof for human reconnection with
nature and well-being are limited [
38
], and further research is required as green roofs
could be a notable method for increasing green space and reconnecting with nature in
urbanized areas.
3.2. Green Roofs and Biodiversity
Studying the ability of green roofs to providing a suitable environment for wildlife
existence appears to be controversial. The scholarly debate has focused on the possibility
of including wildlife in urban spaces through the adoption of green roofs [
9
,
39
,
40
]. Some
early investigations in Germany doubted the ability of green roofs to provide a rich biotic
diversity paradigm [
41
,
42
]. The study questioned the possible depth of the substrate
layers of the artificial roof, as the thinner the substrate layers are, the lower the cost of
green roof construction. At the same time, this can negatively affect the opportunity to
achieve an interconnected biodiverse paradigm. Nevertheless, later studies [
7
,
40
,
43
,
44
]
have demonstrated that a wide spectrum of living species can thrive in green roofs when
these roofs are properly designed with suitable substrate layers, landscape features, plants
and natural elements. For instance, the green roof of Chicago City Hall has the capacity
of accommodating nearly 20,000 plants and more than 150 different types of birds and
invertebrate species living in an area of 2000 m
2
[
45
]. Accordingly, green roofs have been
proposed as an appropriate alternative for adopting wildlife features in urbanized areas.
The scholarly debate has considered the adoption of green roofs in urban spaces as an
alternative to the existence of wildlife in these spaces; yet, more case studies need to be
discussed in order to better understand the practicality and functionality of green roofs as
a valid alternative for wildlife in urban areas.
For better understanding of the impact of green roofs on preserving biodiversity and
achieving biophilia in urban spaces, the case of the High Line Green Roof will be discussed
in this study to derive lessons on the adoption of large-scale green roofs in urban spaces.
Due to the proper scale and the urban value of the High Line, this case has been selected
for thorough investigation in this study.
Urban Sci. 2022,6, 2 5 of 13
4. The High Line
The High Line is a linear elevated urban park and greenway built on a former New
York Central Railroad spur on the west side of the Manhattan in New York city. It has
a length of 1.52 miles and an area of 27.499 m
2
. The structure is mainly steel frames
with reinforced concrete roof decking. The High Line is considered an iconic projects in
New York City. Scientifically, the High Line can be considered a green roof, following the
scientific definition that any top roof of a structure that contains vegetation on the final
layer is regarded as a green roof [33].
The history of the High Line elevated railway has a significant role in the success
of the project refurbishment. The structure was built in the 1930s, when the purpose
of its construction was to improve the urban economy and transportation in the Lower
Manhattan area of New York City [
46
]. The high line railway served to deliver and receive
products from the Meat Packing District [
47
]. The last train movement on this track was
in the 1980s, before a new generation of train were introduced [
48
]. The most significant
part of the High Line’s history starts in the year of 1980, when it stopped working until
1999. Throughout this 20-year timeframe, the High Line roof was abandoned and became
a place for the growth of different types of wildlife plants and other species, showing
the possibility of an emerging biodiverse environment where the required conditions are
available [
47
]. Over the years, some parts of the train tracks were demolished to provide
new areas for development on the site. However, in 1999, Robert Hammond created a
group called Friends of The High Line to preserve the abandoned structure from becoming
demolished [48].
In 2001, the New York City government decided to demolish the entire High Line
site in order to accommodate a new development. The Friends of the High Line strongly
opposed the demolition of the historic project, and provided remarkable financial support
through donation campaigns in order to preserve and redevelop the structure. In 2004, a
design competition was launched aiming to preserve and transform the High Line into a
public urban space. Ultimately, the landscape architect James Corner won the competition
in collaboration with the Field Operations Design Firm [
49
52
]. Figure 2illustrates the
main milestones in the history of the High Line.
Urban Sci. 2022, 5, x FOR PEER REVIEW 6 of 14
Figure 2. History of the High Line in different historical stages. Data from source: [49].
5. Lessons on Biophilia
The concept of the High Line green roof design was based on the principles of
biophilic design, seeking to engage people with nature while retaining the identity of the
place. The proposal involved the creation of a sustainable urban ecology park integrating
people with nature, and with the history of the site inspired by the years that the High
Line was abandoned, resulting in the site becoming obscured by natural vegetation [ibid].
The designers kept the original rails along some parts of the roof in order to preserve its
history. Trees and grass evoke the wildness of nature within the urban context of the New
York City. The pathways have been designed to take different directions and provide
various views of the location, as presented in Figure 3. The architect, James Corner, says
that ‘The High Line is a different place from the rest of New York. There is a sense of
slowness, distraction, and otherworldliness, and that is what we want to preserve’ [53].
Accordingly, the High Line renovation proposal has been designed based on the concept
of biophilia to revive an old construction into a living green roof project.
Figure 3. Design Proposal of the High Line. Reprinted from ref. [50].
Additionally, the High Line Project represents a successful example of green roofs
that engage people with nature. The total number of visitors to the park jumped from 4
Figure 2. History of the High Line in different historical stages. Data from source: [49].
Urban Sci. 2022,6, 2 6 of 13
5. Lessons on Biophilia
The concept of the High Line green roof design was based on the principles of biophilic
design, seeking to engage people with nature while retaining the identity of the place. The
proposal involved the creation of a sustainable urban ecology park integrating people
with nature, and with the history of the site inspired by the years that the High Line was
abandoned, resulting in the site becoming obscured by natural vegetation [ibid]. The
designers kept the original rails along some parts of the roof in order to preserve its history.
Trees and grass evoke the wildness of nature within the urban context of the New York City.
The pathways have been designed to take different directions and provide various views
of the location, as presented in Figure 3. The architect, James Corner, says that ‘The High
Line is a different place from the rest of New York. There is a sense of slowness, distraction,
and otherworldliness, and that is what we want to preserve’ [
53
]. Accordingly, the High
Line renovation proposal has been designed based on the concept of biophilia to revive an
old construction into a living green roof project.
Urban Sci. 2022, 5, x FOR PEER REVIEW 6 of 14
Figure 2. History of the High Line in different historical stages. Data from source: [49].
5. Lessons on Biophilia
The concept of the High Line green roof design was based on the principles of
biophilic design, seeking to engage people with nature while retaining the identity of the
place. The proposal involved the creation of a sustainable urban ecology park integrating
people with nature, and with the history of the site inspired by the years that the High
Line was abandoned, resulting in the site becoming obscured by natural vegetation [ibid].
The designers kept the original rails along some parts of the roof in order to preserve its
history. Trees and grass evoke the wildness of nature within the urban context of the New
York City. The pathways have been designed to take different directions and provide
various views of the location, as presented in Figure 3. The architect, James Corner, says
that ‘The High Line is a different place from the rest of New York. There is a sense of
slowness, distraction, and otherworldliness, and that is what we want to preserve’ [53].
Accordingly, the High Line renovation proposal has been designed based on the concept
of biophilia to revive an old construction into a living green roof project.
Figure 3. Design Proposal of the High Line. Reprinted from ref. [50].
Additionally, the High Line Project represents a successful example of green roofs
that engage people with nature. The total number of visitors to the park jumped from 4
Figure 3. Design Proposal of the High Line. Reprinted from ref. [50].
Additionally, the High Line Project represents a successful example of green roofs
that engage people with nature. The total number of visitors to the park jumped from
4 million people in 2011 to 7 million in 2018 [
54
]. This has led the project to become one of
the most visited places in New York City and on the list of top New York City landmarks
[ibid]. According to online public reviews, it is a highly recommended destination for
visiting (www.tripadvisor.com) (accessed on 10 December 2021). According to the website,
there are more than 60,000 reviews on the project at present; more than 42,000 reviews
have given an excellent rating and 16.000 very good ratings. This amounts to 90% highly
positive reviews on the site. The most popular comments on the site are related to the green
spaces, pleasant walks, and elevated park, which shows the positive view of people about
the space and how they are connected to nature when they walk through it. Following are
samples of reviews of the highline project:
R1: “The walk along the High line is full of lush greenery intermingled with the “concrete
jungle” of high rise buildings. The walking path is well maintained, and is very accessible for
all types of walkers, runners and families with children. The gardens are diverse, with a good
selection of low lying, bush types and taller trees that provide lots of shade and fresh air and
plenty of benches are available for those looking to rest or take in the scenery.”
R2: “An urban green space built on an old railroad. You can still see the railroad structure
remnants. The walk is very peaceful and a great place to reflect on life or have a conversation
with a friend.”
R3: “Not sure what’s all the fuss. Without a doubt, great for the neighborhood to have this
green space in the middle of the city, but I’m not sure why a tourist would go out of their way
to walk along the High Line. Also very crowded and not a relaxing stroll along a relatively
narrow pathway.”
The public reviewers’ comments and the data provided lead to the conclusion that
the Highline successfully connects people with nature by bringing nature to urban areas
where minimal green regions exist. Transforming the old structure into an attractive green
destination is a testament to the project’s success in mimicking nature by having various
types of plants and providing fresh air and relaxation, as suggested by the reviewers.
Urban Sci. 2022,6, 2 7 of 13
To further investigate the project’s biophilic design aspect, a visual analysis of the
project design was undertaken. The analysis was based on measuring the High Line’s views
taking into account the biophilic design patterns discussed earlier in order to investigate
the aspects of biophilia in the project. Hence, photos of the project were collected from
the Friends of the High Line organization’s official website and the photos were visually
analyzed to find biophilic design patterns (https://www.thehighline.org/) (accessed on
10 March 2021). It was observed that the project is highly successful in touching and
applying all of the patterns from the three major categories, namely, Nature in Space,
Natural Analogues and Nature of the Spaces. Figure 4illustrates the visual analysis of
biophilic patterns.
Urban Sci. 2022, 5, x FOR PEER REVIEW 8 of 14
Figure 4. Biophilic patterns of the High Line. Diagram Source: Authors.
Visual observation of people’s interaction with the High Line, on the other hand,
provides further evidence of how green roofs manage to simulate a natural environment.
In [54] it was suggested that most of the visitors of the High Line come for walking and
relaxation purposes, and the study detected a high satisfaction among people visiting the
High Line. The reflections of visitors, as published online, demonstrates the success of the
High line in providing a tangible connection with nature in various forms, as
demonstrated by the remarkable number of visits to this distinguished urban roof. Figure
5 demonstrates the interaction between the visitors and the features and elements of the
High Line green roof.
Figure 4. Biophilic patterns of the High Line. Diagram Source: Authors.
Urban Sci. 2022,6, 2 8 of 13
In studying the aspects of Nature in Space, the High Line shows a high reflection
of visual and non-visual connection with nature, taking into account the wildness of the
views, smells, and sounds of nature. The project evidently encompasses diversity in its
selection of wild plants, the variability of the natural and artificial lights, the cycle of
nature, and seasonal alteration in order to touch human desires related to natural systems
and their variability. The project also incorporates water bodies and wild forms in its
design as important patterns of nature. In terms of its Natural Analogues aspects, the
project includes natural materials in the design of setting objects and excludes synthesized
materials wherever possible. It has also considered the use of organic forms and patterns
evocative of the biomorphic forms and its complicity and order at the same time. It can be
noticed that the Nature of Space has been well-studied in the design of the High line. The
visual analysis attracted the authors’ attention to the design of different activities that take
human attention in nature instinctively. This can be noticed in areas with risk-taking or
the use of mysterious objects and designs that attract visitors to discover, as well as areas
with sheltering and cover spaces to provide a feeling of inclusion to visitors, as presented
in Figure 4.
Visual observation of people’s interaction with the High Line, on the other hand,
provides further evidence of how green roofs manage to simulate a natural environment.
In [
54
] it was suggested that most of the visitors of the High Line come for walking and
relaxation purposes, and the study detected a high satisfaction among people visiting
the High Line. The reflections of visitors, as published online, demonstrates the success
of the High line in providing a tangible connection with nature in various forms, as
demonstrated by the remarkable number of visits to this distinguished urban roof. Figure 5
demonstrates the interaction between the visitors and the features and elements of the
High Line green roof.
Urban Sci. 2022, 5, x FOR PEER REVIEW 9 of 14
Figure 5. People engagement with nature on the top of the High Line. Data from source [49].
The case of the High Line has shown the importance of adopting green roofs as a
substantial alternative to increase greenery in urban spaces and to reconnect people with
nature. The project has shown the ability of green roofs in acting as a valid alternative to
nature in urban areas. The High Line has been successful in attracting visitors to spent
time for relaxation and walking to fulfill their instinctive desires for a connection with
nature, even in urban spaces.
The example of the High Line can be replicated in other urban areas with a planned
Biophilic Urbanism strategy, and green roofs can be a proper alternative for nature when
dense cities fail to increase green land. In addition, the example of the High Line reflects
the essence of Biophilic design patterns as a key measure for the successful design of green
roofs. The more biophilic patterns are implemented, the more the connection with nature
is seen to be sensible. The impact of the High Line in the urban space of New York City is
not limited to reconnection with nature; the High Line has positively impacted the
existence of a more wild and biodiverse environment within the congested urban scheme
of New York City.
6. Lessons on Biodiversity
The emergence of a rich biodiverse environment on the abounded rail line serves as
a lesson on the possibility of the presence of natural wildlife features in a high-end urban
area. The features of wildlife appeared gradually on the surface of the rail line, with
increasing diversity over time. Looking at the timeline of the High Line, the elements of
biodiversity thrived on the surface of the abundant rail line. This was the spark of insight
for the High Line designers to preserve the emerging biodiverse elements and to redefine
them in a proper design scheme, that placed them within the redevelopment scheme.
Another lesson was the impact of strategic planning in preserving biodiversity in urban
spaces. The designers of the High Line embraced a temporal strategy for attracting
different forms of wildlife on the surface of the High Line, in different stages and with
different features; thus, a natural and biodiverse ecosystem thrived. Figure 6 illustrates
the emergence of wildlife features within specific timeframes. As demonstrated in the
diagram, the diversity and integrity of wildlife features increases over the time to include
a wider range of creatures. This process was exemplified in the case of the High Line.
Consequently, the biodiverse environment that has been emerging on the abandoned rail
line has inspired the community to preserve the structure and redesign the rail line in a
way that maintains the biodiversity of the place and presents an interactive urban space
for the citizens of New York City [49–51].
Figure 5. People engagement with nature on the top of the High Line. Data from source [49].
The case of the High Line has shown the importance of adopting green roofs as a
substantial alternative to increase greenery in urban spaces and to reconnect people with
nature. The project has shown the ability of green roofs in acting as a valid alternative to
nature in urban areas. The High Line has been successful in attracting visitors to spent time
for relaxation and walking to fulfill their instinctive desires for a connection with nature,
even in urban spaces.
The example of the High Line can be replicated in other urban areas with a planned
Biophilic Urbanism strategy, and green roofs can be a proper alternative for nature when
dense cities fail to increase green land. In addition, the example of the High Line reflects
the essence of Biophilic design patterns as a key measure for the successful design of green
roofs. The more biophilic patterns are implemented, the more the connection with nature is
seen to be sensible. The impact of the High Line in the urban space of New York City is not
limited to reconnection with nature; the High Line has positively impacted the existence
of a more wild and biodiverse environment within the congested urban scheme of New
York City.
Urban Sci. 2022,6, 2 9 of 13
6. Lessons on Biodiversity
The emergence of a rich biodiverse environment on the abounded rail line serves
as a lesson on the possibility of the presence of natural wildlife features in a high-end
urban area. The features of wildlife appeared gradually on the surface of the rail line, with
increasing diversity over time. Looking at the timeline of the High Line, the elements
of biodiversity thrived on the surface of the abundant rail line. This was the spark of
insight for the High Line designers to preserve the emerging biodiverse elements and
to redefine them in a proper design scheme, that placed them within the redevelopment
scheme. Another lesson was the impact of strategic planning in preserving biodiversity in
urban spaces. The designers of the High Line embraced a temporal strategy for attracting
different forms of wildlife on the surface of the High Line, in different stages and with
different features; thus, a natural and biodiverse ecosystem thrived. Figure 6illustrates the
emergence of wildlife features within specific timeframes. As demonstrated in the diagram,
the diversity and integrity of wildlife features increases over the time to include a wider
range of creatures. This process was exemplified in the case of the High Line. Consequently,
the biodiverse environment that has been emerging on the abandoned rail line has inspired
the community to preserve the structure and redesign the rail line in a way that maintains
the biodiversity of the place and presents an interactive urban space for the citizens of New
York City [4951].
Urban Sci. 2022, 5, x FOR PEER REVIEW 10 of 14
Figure 6. The emergence of a wild and biodiverse ecological system over the time. Reprinted from
ref. [50].
One of the challenges in the redesign of the High Line was the ability to plant various
species within the limited earth layer of the rail line. The Dutch Garden Designer Piet
Oudolf addressed this problem by adopting specific plant types able grow and thrive
within the limited depth of the substrate layers. The average earth depth in the High Line
is 450 mm, and reaches 900 mm in particular locations to accommodate wild trees. Figure
7 illustrates cross-sections for the High Line Garden Roof and shows different substrate
layers from different locations on the roof [49–51].
Figure 7. The High Line: (A) cross-section of the main pathway; (B) cross-section of a multi-level
zone. Reprinted from ref. [50].
The design of the High Line demonstrates another lesson on the possibility of
accommodating various types of wild plants within a limited substrate layer. The rational
use of the available depth in the structure and the proper selection of wild plant types
enabled the generation of a thriving and livable biodiverse environment on the top of the
redesigned High Line. The design adopted seasonal plants of various types, with the aim
of accommodating different living species that find in the seasonal plants a place to
complete their lifecycle, even within a vibrant and crowded urban space. As a result, the
High Line has become a suitable site for different types of migratory and local birds to
grow, feed, and nest on the Green Roof. For instance, the American Kestrel, House
Sparrow, Mourning Dove, Northern Mockingbird and Peregrine Falcon are among the
types of birds living along the High Line. This demonstrates another lesson on the
importance of adopting various planting strategies that match with all the seasons in order
to achieve a rich ecological environment that accommodates different forms of wildlife in
the urban space.
James Corner, the design architect, and the design team have outlined the High Line
design to reflect different microclimatic conditions [52]. Along the linear landscape of the
High Line, multiple climatic zones have been presented, each with the features and
Figure 6.
The emergence of a wild and biodiverse ecological system over the time. Reprinted from
ref. [50].
One of the challenges in the redesign of the High Line was the ability to plant various
species within the limited earth layer of the rail line. The Dutch Garden Designer Piet
Oudolf addressed this problem by adopting specific plant types able grow and thrive
within the limited depth of the substrate layers. The average earth depth in the High Line
is 450 mm, and reaches 900 mm in particular locations to accommodate wild trees. Figure 7
illustrates cross-sections for the High Line Garden Roof and shows different substrate
layers from different locations on the roof [4951].
Urban Sci. 2022,6, 2 10 of 13
Urban Sci. 2022, 5, x FOR PEER REVIEW 10 of 14
Figure 6. The emergence of a wild and biodiverse ecological system over the time. Reprinted from
ref. [50].
One of the challenges in the redesign of the High Line was the ability to plant various
species within the limited earth layer of the rail line. The Dutch Garden Designer Piet
Oudolf addressed this problem by adopting specific plant types able grow and thrive
within the limited depth of the substrate layers. The average earth depth in the High Line
is 450 mm, and reaches 900 mm in particular locations to accommodate wild trees. Figure
7 illustrates cross-sections for the High Line Garden Roof and shows different substrate
layers from different locations on the roof [49–51].
Figure 7. The High Line: (A) cross-section of the main pathway; (B) cross-section of a multi-level
zone. Reprinted from ref. [50].
The design of the High Line demonstrates another lesson on the possibility of
accommodating various types of wild plants within a limited substrate layer. The rational
use of the available depth in the structure and the proper selection of wild plant types
enabled the generation of a thriving and livable biodiverse environment on the top of the
redesigned High Line. The design adopted seasonal plants of various types, with the aim
of accommodating different living species that find in the seasonal plants a place to
complete their lifecycle, even within a vibrant and crowded urban space. As a result, the
High Line has become a suitable site for different types of migratory and local birds to
grow, feed, and nest on the Green Roof. For instance, the American Kestrel, House
Sparrow, Mourning Dove, Northern Mockingbird and Peregrine Falcon are among the
types of birds living along the High Line. This demonstrates another lesson on the
importance of adopting various planting strategies that match with all the seasons in order
to achieve a rich ecological environment that accommodates different forms of wildlife in
the urban space.
James Corner, the design architect, and the design team have outlined the High Line
design to reflect different microclimatic conditions [52]. Along the linear landscape of the
High Line, multiple climatic zones have been presented, each with the features and
Figure 7.
The High Line: (
A
) cross-section of the main pathway; (
B
) cross-section of a multi-level
zone. Reprinted from ref. [50].
The design of the High Line demonstrates another lesson on the possibility of accom-
modating various types of wild plants within a limited substrate layer. The rational use of
the available depth in the structure and the proper selection of wild plant types enabled the
generation of a thriving and livable biodiverse environment on the top of the redesigned
High Line. The design adopted seasonal plants of various types, with the aim of accom-
modating different living species that find in the seasonal plants a place to complete their
lifecycle, even within a vibrant and crowded urban space. As a result, the High Line has
become a suitable site for different types of migratory and local birds to grow, feed, and nest
on the Green Roof. For instance, the American Kestrel, House Sparrow, Mourning Dove,
Northern Mockingbird and Peregrine Falcon are among the types of birds living along
the High Line. This demonstrates another lesson on the importance of adopting various
planting strategies that match with all the seasons in order to achieve a rich ecological
environment that accommodates different forms of wildlife in the urban space.
James Corner, the design architect, and the design team have outlined the High Line
design to reflect different microclimatic conditions [
52
]. Along the linear landscape of
the High Line, multiple climatic zones have been presented, each with the features and
characteristics of that particular zone. For instance, the Falcone Flyover zone is a wet-shaded
climatic zone that accommodates wild forest trees, while the Sun lawn zone is a dry–sunny
climatic zone that accommodates wild high grasses and seasonal flowers, as shown in
Figure 8. The variety of climatic zones in the High Line reflects the essence of mimicking
different climatic conditions in the design of urban spaces to allow the flourishing of a
biodiverse environment. The High Line design has successfully reflected various climatic
conditions in the different zones of the design, presenting a holistic and comprehensive
picture of biodiversity [4952].
Figure 8. The High Line: (A) Sun Lawn Zone; (B) Falcone Flyover Zone. Data from source [49].
Urban Sci. 2022,6, 2 11 of 13
Today, the High Line Green Roof is seen as a successful paradigm for bringing wildlife
into urban spaces. The artificial alternative greenspace has reflected an effective and
practical approach for the emergence and thriving of a biodiverse environment within the
urban scheme. Having adequate conditions and proper design elements, green roofs can
substantially enhance the biodiversity of public urban spaces. The lessons reflected in this
study on biophilia and biodiversity demonstrate the success factors behind the High Line
Green Roof. These lessons can be transferred to and implemented in other urban areas
where the aim is to reconnect with the nature and conserve biodiversity in the urban area.
7. Conclusions
Urbanization has notably impacted the connection of human beings with nature, as
well as the existence of wildlife and biodiversity in urban spaces. The adoption of green
roofs in urban areas is seen to be one of the substantial aspects of sustainable urban design
that could significantly answer the call for tangible reconnection with nature as well as
tackle the challenges of climate changes caused by urbanization. This study has attempted
to reflect lessons on the implementation of green roofs in urban spaces based on a case
study. The study has yielded the conclusions drawn below.
First, green roofs have proven to be a substantial alternative method for increasing
greenery in urban spaces and reconnecting people with nature. The case study presented a
successful project that is able to attract visitors to spent time in relaxation and walking and
fulfill their instinctive desires for the natural environment in an urban space.
Second, the example of the High Line can be replicated through Biophilic Urbanism
(BU) when dense cities fail to increase green land, by using alternative GIs such as green
walls, roofs, and balconies. However, pre-planning is essential before any applications for
the success of this strategy.
Third, biophilic design patterns can be used as a key measure to design green roofs,
and should take the maximum number of biophilic patterns into design consideration,
namely, Nature in Space, Natural Analogues, and Nature of Space. This, in return, will aid
in reconnection with nature in urban areas.
Fourth, with a proper design strategy and adequate conditions green roofs can ac-
commodate a thriving and biodiverse environment within urban areas. The variety of soil
depth and different microclimate conditions in green roofs can help accommodate different
types of plants, insects, birds, and other animals accordingly. Such design strategies are
critical for the creation of a rich ecological area.
Fifth, although green roofs are human-made structures, these structures have shown
the ability to mimic the features and characteristics of wild areas. The diversity of planting
in the different site zones and the existence of living species actively depict the features
of wildlife.
Finally, the adoption of green roofs in the design of urban areas can be a competent
alternative to the existence of nature in the urban scheme. However, further research is rec-
ommended in order to investigate and discuss the challenges and barriers in transforming
this approach to other urban areas.
Author Contributions:
Conceptualization, K.S.; methodology, K.S., software, K.S. and Z.O.S.; valida-
tion, K.S., Z.O.S. and A.A.; formal analysis, K.S. and Z.O.S.; investigation, K.S. and Z.O.S.; resources,
K.S. and Z.O.S.; data curation, K.S. and Z.O.S.; writing—original draft preparation, K.S.; writing—
review and editing, K.S., Z.O.S. and A.A.; visualization, K.S. and Z.O.S.; supervision, K.S.; project
administration, K.S. All authors have read and agreed to the published version of the manuscript.
Funding: This research received no external funding.
Institutional Review Board Statement: Not applicable.
Informed Consent Statement: Not applicable.
Data Availability Statement: Not applicable.
Conflicts of Interest: The authors declare no conflict of interest.
Urban Sci. 2022,6, 2 12 of 13
References
1. Ritchie, A.; Thomas, R. Sustainable Urban Design: An Environmental Approach; Taylor & Francis: London, UK, 2013.
2. IEA. CO2Emissions from Fuel Combustion: Overveiw; IEA: Paris, France, 2020.
3. Ren, G. Urbanization as a major driver of urban climate change. Adv. Clim. Change Res. 2017,6, 1–6. [CrossRef]
4. Argüeso, D.; Evans, J.P.; Pitman, A.J.; di Luca, A. Effects of city expansion on heat stress under climate change conditions. PLoS
ONE 2015,10, e0117066. [CrossRef] [PubMed]
5.
Depietri, Y.; McPhearson, T. Integrating the Grey, Green, and Blue in Cities: Nature-Based Solutions for Climate Change Adaptation
and Risk Reduction, in Nature-Based Solutions to Climate Change Adaptation in Urban Areas; Springer: Cham, Switzerland, 2017;
pp. 91–109.
6.
Langemeyer, J.; Wedgwood, D.; McPhearson, T.; Baró, F.; Madsen, A.L.; Barton, D.N. Creating urban green infrastructure where it
is needed—A spatial ecosystem service-based decision analysis of green roofs in Barcelona. Sci. Total Environ.
2020
,707, 135487.
[CrossRef] [PubMed]
7.
Ksiazek-Mikenas, K.; Herrmann, J.; Menke, S.B.; Köhler, M. If you build it, will they come? plant and arthropod diversity on
urban green roofs over time. Urban Nat. 2018,1, 52–72.
8.
Susca, T. Green roofs to reduce building energy use? A review on key structural factors of green roofs and their effects on urban
climate. Build. Environ. 2019,162, 106273. [CrossRef]
9.
Mayrand, F.; Clergeau, P.J.S. Green roofs and green walls for biodiversity conservation: A contribution to urban connectivity?
Sustainability 2018,10, 985. [CrossRef]
10.
Sanchez, L.; Reames, T.G.J.U.F.; Greening, U. Cooling Detroit: A socio-spatial analysis of equity in green roofs as an urban heat
island mitigation strategy. Urban For. Urban Green. 2019,44, 126331. [CrossRef]
11.
Hashemi, S.S.G.; Mahmud, H.B.; Ashraf, M.A. Performance of green roofs with respect to water quality and reduction of energy
consumption in tropics: A review. Renew. Sustain. Energy Rev. 2015,52, 669–679. [CrossRef]
12.
Baraldi, R.; Neri, L.; Costa, F.; Facini, O.; Rapparini, F.; Carriero, G. Ecophysiological and micromorphological characterization of
green roof vegetation for urban mitigation. Urban For. Urban Green. 2019,37, 24–32. [CrossRef]
13.
Blank, L.; Vasl, A.; Levy, S.; Grant, G.; Kadas, G.; Dafni, A.; Blaustein, L. Directions in green roof research: A bibliometric study.
Build. Environ. 2013,66, 23–28. [CrossRef]
14.
Zhang, X.; Shen, L.; Tam, V.W.Y.; Lee, W.W.Y. Barriers to implement extensive green roof systems: A Hong Kong study. Renew.
Sustain. Energy Rev. 2012,16, 314–319. [CrossRef]
15. Rowe, D.B. Green roofs as a means of pollution abatement. Environ Pollut. 2011,159, 2100–2110. [CrossRef]
16.
Vijayaraghavan, K. Green roofs: A critical review on the role of components, benefits, limitations and trends. Renew. Sustain.
Energy Rev. 2016,57, 740–752. [CrossRef]
17.
Willemsen, E.; Tillie, N. Reconnecting green: Towards a multi-dimensional biophilic city. In Proceedings of the IIFLA Conference,
Singapore, 18–21 July 2018.
18.
Snep, R.P.; Clergeau, P. Biodiversity in cities, reconnecting humans with nature. In Sustainable Built Environments; Springer: New
York, NY, USA, 2020; pp. 251–274.
19.
Lehmann, S. Reconnecting with nature: Developing urban spaces in the age of climate change. Emerald Open Res.
2019
,1, 2.
[CrossRef]
20.
Lehmann, S. Reconnecting cities with nature, building resilience at the urban scale. In Urban Regeneration; Springer: Cham,
Switzerland, 2019; pp. 55–77.
21. Kellert, S.R. The Biophilia Hypothesis; Island Press: Washington, DC, USA, 1995.
22. Kellert, R.S.; Heerwagen, J.; Mador, M. Biophilic Design: The Theory, Science and Practice of Bringing Buildings to Life; John Wiley &
Sons: Hoboken, NJ, USA, 2011.
23. Ulrich, R.S. View through a window may influence recovery from surgery. Science 1984,224, 420–421. [CrossRef] [PubMed]
24.
Roe, J.; Aspinall, P. The restorative benefits of walking in urban and rural settings in adults with good and poor mental health.
Health Place 2011,17, 103–113. [CrossRef] [PubMed]
25. Beatley, T. Biophilic Cities: Integrating Nature into Urban Design and Planning; Island Press: Washington, DC, USA, 2011.
26. Newman, P. Biophilic urbanism: A case study on Singapore. Aust. Plan. 2014,51, 47–65. [CrossRef]
27.
Kellert, S.; Calabrese, E. The Practice of Biophilic Design. 2015. Available online: http://docs.wixstatic.com/ugd/21459d_81ccb8
4caf6d4bee8195f9b5af92d8f4.pdf (accessed on 26 December 2021).
28.
Ryan, C.O.; Browning, W.D.; Clancy, J.O.; Andrews, S.L.; Kallianpurkar, N.B. Biophilic design patterns: Emerging nature-based
parameters for health and well-being in the built environment. Int. J. Archit. Res. 2014,8, 62. [CrossRef]
29.
Savard, J.-P.L.; Clergeau, P.; Mennechez, G. Biodiversity concepts and urban ecosystems. Landsc. Urban Plan.
2000
,48, 131–142.
[CrossRef]
30.
Sol, D.; González-Lagos, C.; Moreira, D.; Maspons, J.; Lapiedra, O. Urbanisation tolerance and the loss of avian diversity. Ecol.
Lett. 2014,17, 942–950. [CrossRef]
31.
Concepción, E.D.; Moretti, M.; Altermatt, F.; Nobis, M.P.; Obrist, K.M. Impacts of urbanisation on biodiversity: The role of species
mobility, degree of specialisation and spatial scale. OIKOS Adv. Ecol. 2015,124, 1571–1582. [CrossRef]
32. Hardman, S. How does urbanisation affect biodiversity. Ecologica, 6 November 2011.
33. Cavanaugh, L.M. Redefining the Green Roof. J. Archit. Eng. 2008,14, 4–6. [CrossRef]
Urban Sci. 2022,6, 2 13 of 13
34.
Berardi, U.; GhaffarianHoseini, A.H.; GhaffarianHoseini, A. State-of-the-art analysis of the environmental benefits of green roofs.
Appl. Energy 2014,115, 411–428. [CrossRef]
35.
Newman, P.; Beatley, T.; Boyer, H. Build Biophilic Urbanism in the City and Its Bioregion. In Resilient Cities; Springer: Cham,
Switzerland, 2017; pp. 127–153.
36.
Mentens, J.; Raes, D.; Herm, M. Green roofs as a tool for solving the rainwater runoff problem in the urbanized 21st century?
Landsc. Urban Plan. 2006,77, 217–226. [CrossRef]
37.
Matsunaga, K.; Park, B.-J.; Kobayashi, H.; Miyazaki, Y. Physiologically relaxing effect of a hospital rooftop forest on older women
requiring care. J. Am. Geriatr. Soc. 2011,59, 2162–2163. [CrossRef]
38.
Manso, M.; Teotónio, I.; Silva, C.M.; Cruz, C.O. Green roof and green wall benefits and costs: A review of the quantitative
evidence. Renew. Sustain. Energy Rev. 2021,135, 110111. [CrossRef]
39. Brenneisen, S. Space for urban wildlife: Designing green roofs as habitats in Switzerland. Urban Habitats 2006,4, 27–36.
40.
Partridge, D.R.; Clark, J.A. Urban green roofs provide habitat for migrating and breeding birds and their arthropod prey. PLoS
ONE 2018,13, e0202298. [CrossRef] [PubMed]
41.
Riedmiller, J. Untersuchungen zur Anlage, Besiedelung und Vernetzung von Anthropogenen Sekundärbiotopen auf Dachflächen; Heidelberg
University: Heidelberg, Germany, 1994.
42. Mann, G. Vorkommen und Bedeutung von Bodentieren (Makrofauna) auf Begrünten Dächern in Anhängigkeit von der Vegeta-
tionsform (Occurence and Significance of Soil Organisms (Macrofauna) on Green Roofs in Response to Vegetation Type). Ph.D.
Thesis, Eberhard Karls Universität Tübingen, Tübingen, Germany, 1998.
43. Cook-Patton, S.C. Plant biodiversity on green roofs. In Green Roof Ecosystems; Springer: Cham, Switzerland, 2015; pp. 193–209.
44.
Köhler, M.; Ksiazek-Mikenas, K. Green roofs as habitats for biodiversity. In Nature Based Strategies for Urban and Building
Sustainability; Elsevier: Amsterdam, The Netherlands, 2018; pp. 239–249.
45. Miller, J.R. Biodiversity conservation and the extinction of experience. Trends Ecol. Evol. 2005,20, 430–434. [CrossRef]
46.
Sternfeld, J. Design Trust Fellow: Casey Jones. 2002. Available online: https://www.solaripedia.com/files/1048.pdf (accessed on
26 December 2021).
47.
Farley, L. Urban Simulation Techonologies and High Line. 2009. Available online: https://research.gsd.harvard.edu/zofnass/
files/2013/05/efarley-urban-simulation.pdf (accessed on 26 December 2021).
48.
Brooks, G. Reusing and Repurposing New York City’s Infrastructure: Case Studies of Reused Transportation Infrastructure; Wagner: New
York, NY, USA, 2010; 27p.
49. The High Line. 2021. Available online: https://www.thehighline.org (accessed on 2 March 2021).
50.
The High Line. 2011. Available online: https://summerssce10.files.wordpress.com/2010/06/highline-part-1.pdf?fbclid=IwAR0
y3GYWrnYCCg_hDuTizJxteyOQuxrFjjAfKPaNSuKyFJtXoKd0htZYsXE (accessed on 1 March 2021).
51.
Millington, N. From urban scar to ‘park in the sky’: Terrain vague, urban design, and the remaking of New York City’s High Line
Park. Environ. Plan. A Econ. Space 2015,47, 2324–2338. [CrossRef]
52.
Cortés-Cediel, E.M.; Cantador, I.; Bolívar, M.P.R. Analyzing Citizen Participation and Engagement in European Smart Cities. Soc.
Sci. Comput. Rev. 2021,39, 592–626. [CrossRef]
53.
Iovine, J.V. ARCHITECTURE: Elevated Visions. 2004. Available online: https://www.nytimes.com/2004/07/11/arts/
architecture-elevated-visions.html?fbclid=IwAR06TWYOUlw1Gmw0rjlmGIXzRlecHa_UbBToEQWK97lK1cBOvsfElA7EYH4
(accessed on 1 March 2021).
54.
Sim, J.; Bohannon, C.L.; Miller, P.J.S. What Park Visitors Survey Tells Us: Comparing Three Elevated Parks—The High Line, 606,
and High Bridge. Sustainability 2020,12, 121. [CrossRef]
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... Green areas could be also increased. One key feature is green roofs, which decrease rainwater runoff and reduce the heat island effect (Salih et al., 2022). The cooling effect of urban greenery has been analysed at three scales: the block scale, such as streets, the neighbourhood scale, and the city scale (Licón-Portillo et al., 2024). ...
... Our study showed that green roofs have the potential to become valuable reservoirs of fungal biodiversity, with green roofs having higher diversity than the ground level. The potential for green roofs to act as biodiversity reservoirs has been discussed at length (Benvenuti, 2014;Brenneisen, 2006;Francis & Lorimer, 2011;Ksiazek-Mikenas et al., 2018;Madre et al., 2014;Salih et al., 2022), although some researchers caution against overselling this ecosystem service for green roofs in conservation and policy planning due to the lack of widespread implementation and long-term research (Henry & Frascaria-Lacoste, 2012;Williams et al., 2014). Our findings show that green roofs could be useful in maintaining ground-level fungal diversity in the urban landscape. ...
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Green roof soils are usually engineered for purposes other than urban biodiversity, which may impact their fungal communities, and in turn impact the health of plants in the urban ecosystem. We examined the drivers of fungal diversity and community composition in soil of green roofs and adjacent ground‐level green spaces in three Midwestern USA cities – Chicago, Cleveland, and Minneapolis. Overall, fungal communities on green roofs were more diverse than ground‐level green spaces, and were correlated with plant cover (positively) and roof age (negatively) rather than abiotic soil properties. Fungal community composition was distinct between roof and ground environments, among cities, and between sampling sites, but green roofs and their immediately surrounding ground‐level green space showed some similarity. This suggests dispersal limitation may result in geographic structure at large spatial scales, but dispersal between roofs and their neighboring sites may be occurring. Different fungal taxonomic and functional groups were better explained when roofs were classified either by depth (extensive or intensive) or functional intent of the roof design (i.e., stormwater/energy, biodiversity, or aesthetics/recreation). Our results demonstrate that green roofs are an important reservoir of fungal diversity in the urban landscape, which should be considered in future green roof design. This article is protected by copyright. All rights reserved.
Chapter
This chapter closely examines the crucial role of integrating green infrastructure in enhancing urban resilience amidst the contemporary challenges faced by cities. These challenges highlight problems relating to climate change, urban sprawl, etc. within the boundaries of limited resource constraints. The chapter starts by examining the crucial role of green infrastructure in mitigating these challenges. The scope and historical evolution of green infrastructure in urban planning has also been discussed. It thereby provides a background for its contemporary relevance and adoption. It further examines the ecological aids of green infrastructure, emphasizing its capacity to mitigate the urban heat island effect, improve water and air quality, conserve biodiversity, and facilitate natural storm water management. The chapter also discusses some of the contemporary green infrastructure projects and their positive impacts on local ecosystems. It further deliberates upon the economic advantages of green infrastructure, evaluating its cost-effectiveness and social benefits as compared to traditional urbanization. The subsequent section focuses on policy implications, emphasizing upon the fact that integration of green infrastructure needs to be augmented into urban policies. This can be done through issuance of regulatory guidelines, and by devising incentive schemes with regard to urban real estate development. It also proposes the need for educating the general masses in this context. The chapter explores future directions and innovations, examines emerging trends and technological advancements in the field of green infrastructure. The final section summarizes key findings and issues; and highlights the importance of integrating green infrastructure in future urban planning.
Conference Paper
With climate change and extreme weather events resulting from it, a strong demand for urbanization due to a steadily increasing population, cities face a number of complex challenges in responding to current issues and preparing for future needs. Green Infrastructure (GI) have been identified as a useful tool to cope with the effects of climate change. They are positioned as a possible alternative to grey infrastructure. A GI is able to provide a multiplicity of benefits and functionalities that can be assimilated with what emerges from the definitions of Ecosystem Services (ES). Numerous studies, in an attempt to find an unambiguous definition of GI, have developed the concept of a grey-green continuum that underlines the link between green and grey infrastructures. The aim of this paper is to focus on the concept of continuum in order to identify the correct nuance depending on the required benefit and boundary conditions. Furthermore, it is highlighted that variability does not invalidate sustainability as a goal to be achieved. Based on this assumption, three best projects of disused grey urban infrastructure that are given new value will be investigated - social, economic and environmental. The High Line in New York, Seoullo 7017 Skygarden in Seoul and the Xuhui Runway Park in Shanghai represent the three case studies in which a balance between GI and grey infrastructure is noticeable. For each we highlight which path has been followed for a green reconversion.
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Many cities have replaced abandoned transportation infrastructure with an elevated park to gain increased economic benefits by developing old fabric. By following this trend, most studies to this point have only focused on the economic rewards from the replacement rather than its uses in the real world. This study aims to understand how park visitors use elevated parks through a park visitors’ survey. The authors selected three representative elevated parks—the High Line in New York City, the 606 in Chicago, and the High Bridge in Farmville—for the study and asked visitors about their activities, perceived benefits, and satisfaction. Results indicate that the 606, a mixed-use elevated park, allows visitors to engage in high-intensity activity, the High Line as an elevated urban park provides visitors public arts and gardens, and the High Bridge as an elevated green park provided visitors with a connection to unique natural scenery. This study, as the first to compare three different elevated parks, contributes to an understanding of who uses elevated parks and how they use elevated parks.
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With the advent of smart cities (SCs), governance has been placed at the core of the debate on how to create public value and achieve a high quality of life in urban environments. In particular, given that public value is rooted in democratic theory and new technologies that promote networking spaces have emerged, citizen participation represents one of the principal instruments to make government open and close to the citizenry needs. Participation in urban governance has undergone a great development: from the first postmodernist ideals of countering expert dominance to today’s focus on learning and social innovation, where citizen participation is conceptualized as co-creation and co-production. Despite this development, there is a lack of research to know how this new governance context is taking place in the SC arena. Addressing this situation, in this article, we present an exhaustive survey of the research literature and a deep study of the experience in participative initiatives followed by SCs in Europe. Through an analysis of 149 SC initiatives from 76 European cities, we provide interesting insights about how participatory models have been introduced in the different areas and dimensions of the cities, how citizen engagement is promoted in SC initiatives, and whether the so-called creative SCs are those with a higher number of projects governed in a participatory way.
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Climate change is occurring around us and impacting on our daily lives, meaning that we have to deal with our cities in a different way. There is also increasing awareness of the need for daily contact with green spaces and the natural environment in order to live a happy, productive and meaningful life. This reflective essay tells the narrative of how urbanisation has been disconnecting humans from nature. Non-sustainable, non-resilient patterns of urbanisation, along with the neglect of inner-city areas, have resulted in fragmentation and urban decline, led to a loss of biodiversity, and caused the deterioration of ecosystems and their services. Urban regeneration projects allow us to “repair” and restore some of this damage whilst enhancing urban resilience. Connecting existing and enhanced ecosystems, and re-establishing ecosystems both within cities and at the peri-urban fringe is vital for strengthening ecosystem resilience and building adaptive capacity for coping with the effects of climate change. Cities worldwide need to look for suitable solutions to increase the resilience of their urban spaces in the face of climate change. This essay explores how this can be achieved through the integration of nature-based solutions, the re-greening of neighbourhoods and by correctly attributing value to natural capital. Transforming existing cities and neighbourhoods in this way will enable ecosystems to contribute their services towards healthier and more liveable cities.
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Greening the urban environment can be an important strategy to tackle the problems of urban densification and meet the United Nations Sustainable Development Goals. Green infrastructures, like green roofs and green walls, have multiple associated environmental, social and economic benefits that improve buildings performance and the urban environment. Yet, the implementation of green roofs and green walls is still limited, as these systems often have additional costs when compared to conventional solutions. Recent studies have been comparing these greening systems to other solutions, balancing the long-term benefits and costs. Also, there is significant research on green roofs and green walls benefits. Although, green roofs and green walls economic analyses don't include all benefits due to measuring difficulties. The associated uncertainty regarding the quantification of the benefit makes it difficult to compare the research outcomes. This paper aims to provide a research review of existing benefits and costs of different types of green roofs and green walls. These were divided between building scale benefits, urban scale benefits and life cycle costs, focusing on the identification of results variability and assessment of their average quantification. The analysis shows that in general, there are few data regarding intangible benefits, as the promotion of quality of life and well-being. Also, there are still few studies quantifying green walls benefits and costs. High variability in data is mostly related to the different characteristics of systems, buildings envelope, surrounding environment and local weather conditions.
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As cities face increasing pressure from densification trends, green roofs represent a valuable source of ecosystem services for residents of compact metropolises where available green space is scarce. However, to date little research has been conducted regarding the holistic benefits of green roofs at a citywide scale, with local policymakers lacking practical guidance to inform expansion of green roofs coverage. The study addresses this issue by developing a spatial multi-criteria screening tool applied in Barcelona, Spain to determine: 1) where green roofs should be prioritized in Barcelona based on expert elicited demand for a wide range of ecosystem services and 2) what type of design of potential green roofs would optimize the ecosystem service provision. As inputs to the model, fifteen spatial indicators were selected as proxies for ecosystem service deficits and demands (thermal regulation, runoff control, habitat and pollination, food production, recreation, and social cohesion) along with five decision alternatives for green roof design (extensive, semi-intensive, intensive, naturalized, and allotment). These indicators and alternatives were analyzed probabilistically and spatially, then weighted according to feedback from local experts. Results of the assessment indicate that there is high demand across Barcelona for the ecosystem services that green roofs potentially might provide, particularly in dense residential neighborhoods and the industrial south. Experts identified habitat, pollination and thermal regulation as the most needed ES with runoff control and food production as the least demanded. Naturalized roofs generated the highest potential ecosystem service provision levels for 87.5% of rooftop area, apart from smaller areas of central Barcelona where intensive rooftops were identified as the preferable green roof design. Overall, the spatial model developed in this study offers a flexible screening based on spatial multi-criteria decision analysis that can be easily adjusted to guide municipal policy in other cities considering the effectiveness of green infrastructure as source of ecosystem services.
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Multiple studies have quantified the ecosystem services of green infrastructure for both public and environmental health. This study evaluates and compares accessibility of low-income and marginalized communities to the cooling benefits of green roofs in Detroit, MI in the context of the urban heat island effect and the City’s current heat relief system of dedicated cooling centers. Regions of the city were evaluated for their vulnerability to the urban heat island effect, which can be alleviated by green roofs due to raised surface albedo and evaporative cooling. Spatial data regarding land surface temperature, income, and race were used to locate where green roof ecosystem services are most needed and how communities within these regions are categorized demographically. Existing green roof efforts were mapped to determine whether siting has occurred where ecosystem services are most needed and how socioeconomic factors might be related to the locations of urban heat island-mitigating green infrastructure. Analysis of the spatial data in this study revealed most low-income residents are within walking distance from cooling centers, but not included in the Detroit Future City Urban Green Neighborhoods, while green roofs specifically were in the affluent part of Detroit's urban core, where the population is predominantly white. The methodology employed here can be applied to evaluate urban greening plans in other cities. More here https://urbanenergyjusticelab.com/research/publications/
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In the next decades, the increase in global population will lead to further urbanization determining, on the one hand, an increase in building energy use and, on the other hand, a surge in urban temperature, which, in turn, affects building energy demand. Since the building sector greatly contributes to the use of energy globally, the amelioration of this sector is an urgent issue to contribute to climate stabilization. Published literature shows that green roofs affect both directly and indirectly building energy use, delivering the message that green roofs are fit-all solutions. However, the efficacy of the deployment of green roofs varies depending on climate and on their specific design. The present study contains a geographically explicit review of the potential building energy benefits deriving by the installation of green roofs depending on their specific design aiming at answering to the following research questions: - Are green roofs fit-all solutions for decreasing building energy use in diverse climates? - How insulation, growing media, and plant selection of green roofs should be calibrated in different climates to maximize their effect on building energy use? - How green roofs can contribute to urban heat island-mitigation in different climates? Answering these research-questions, this study provides urban decision-makers and planning agencies useful insights to, not only prioritize strategies, but also efficiently design by-laws and local regulations to maximize the potential positive effect of urban-wide green roof deployment on building energy use.
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Unsustainable, non-resilient urbanisation patterns and the neglect of inner-city urban areas have caused fragmentation, depletion and urban decline, led to humankind overpowering nature, causing biodiversity loss and the degradation of ecosystems and their services. Urban regeneration projects allow us to ‘repair’ and restore some of this damage while enhancing urban resilience. For instance, increasing connectivity between existing and enhanced ecosystems and restoring them within cities and at the peri-urban fringe (e.g. through nature-based solutions and the re-naturing of neighbourhoods) is necessary to strengthen ecosystem resilience and the adaptive capacity to cope with the effects of climate change. There is growing recognition of the need for daily contact with green spaces and nature in order to live happy, productive and meaningful lives.