Marie Davidová and Kateřina Zímová COLridor
https://doi.org/10.7577/formakademisk.2647
Marie Davidová and Kateřina Zímová
COLridor
Co-design and co-living urban adaptation
Abstract
The mission of the present trans-disciplinary community environmental project COLridor
(Davidová, 2017b) is to generate a situation of eco-systemic co-living across local species and
the abiotic agency in an urban environment through their co-design. Located in the city centre
of Prague, the case study bio-tope is part of larger bio-corridor that has evolved, namely due
to the adjacent railway and water stream. Though the prevailing opinion of European urbanists
is that cities should remain dense and separate from the rest of nature, landscape ecologists
and biologists tend to disagree. There is no nature on Earth without human beings, and these
together evolved, reflecting each other’s impacts and interactions. Therefore, there is also no
social justice without the environmental one and vice versa. A large variety of species have
adapted and evolved for life in the urban environment, which at the moment for many, offers a
safer and more habitable living environment than agricultural land with its herbicides, pests,
antibiotics and antibiotic-resistant bacteria. Through systematically co-designed and cocreated so-called eco-systemic ‘prototypical urban interventions’ (Doherty, 2005), the project
aims to motivate the generation of an edible landscape and a social, cultural and habitable
urban environment across species. It is claimed here that designers should no longer be
designing for but rather designing with the overall eco-system. This case study helps justify the
first author’s ratified design field Systemic Approach to Architectural Performance, covering
a fusion of a variety of co-designs across the eco-system in process-based fields.
This is an extended, edited and updated article based on the working paper ‘COLridor:
Co-Design and Co-Living for Sustainable Futures’ (Davidová & Zímová, 2017) for Relating
Systems Thinking and Design 6 Conference within the theme ‘Environment, Economy,
Democracy: Flourishing Together’ (Sevaldson, 2017a).
Keywords: Systemic Approach to Architectural Performance; Eco-Systemic Agency; Systems
Oriented Design, Performance Oriented Design; GIGA-Mapping, Eco-Systemic Urban
Interventions; Eco-Systemic Co-Design; Landscape Ecology; Biodiversity; Climate Change
Adaptation; Public Engagement; Responsive Wood.
Introduction
The old garden of the loghouse Zvonařka with adjacent Nusle Stairs is Prague’s nature-like biotope1 with remarkable diversity (see Figure 1), and along with the adjacent railway, parks and
gardens, it generates a rare bio-corridor2 within the city centre. As it is located in one of the
most expensive residential areas, the pressure on its building development is high. In 2011, a
large apartment complex design was submitted for permit, arguing ‘for keeping the greenery
character due to its green roofs’ (RH-Arch, 2011). This induced vast community protests as
both the house as well as the garden are listed as historical heritage. Furthermore, it covers ‘ecosystemic services’ in the location (see Figure 1). There is evidence that human life cannot exist
without these services (Sandhu & Wratten, 2013); however, neither the previous nor a recently
proposed metropolitan plan lists the area for protection (Institute of Planning and Development
Prague, 2016). Based on a personal conversation with its creators, the Institute of Planning and
Development Prague is interested in increasing the city’s density, not extending its biocorridors and bio-diversity within the city centre. This plan is neither co-designed with
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ecologists nor with local communities or Non-Governmental Organisations (the finalised
version is available for commenting or complaints without any commitment to change). Purely
urbanists, marking the areas in the plan from their tables, without investigating the areas, have
created it. As also confirmed by the Concept of Metropolitan Plan Justification, the plan does
not consider ‘details’ (Kubeš et al., 2014). It also states that due to being behind the range of
land planning, the design is not in accordance with the European Commission’s strategy of
Green Infrastructure (European Commission, 2010). Instead, the term ‘Landscape
Infrastructure’ is used (Kubeš et al., 2014). This term is not in accordance with the complexity
of the strategy, while, as mentioned, contributions from disciplines other than from urbanists
and local communities are fully excluded.
Figure 1. The first author is giving a speech on Bio-Corridor’s importance during the local community
meeting at Nusle Stairs (photo: Michálková 2016).
It is argued that the recent common understanding of eco-systemic services should be revised.
The authors agree with Metzger, who stated that the Ecosystem Services Approach is currently
based on a thoroughly modernist conception of the world (Metzger, 2017). Eco-systemic
services are perceived mainly from an anthropocentric perspective, mapping only the
performance that is directed towards humans, such as a park with grass cut to a two-centimetre
height for good picnicking and all its biological rotten waste from trees, for example, is removed
due to hygienic or safety reasons. This does not provide any eco-systemic services for the
majority of actors within the eco-system. As such, it does not offer any nutrients, habitation or
even opportunities for relaxation for any species other than the human species.
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Investigating this discussion, the first author’s,at that time, purely architectural NGO
Collaborative Collective (Collaborative Collective, 2012, 2016; Davidová, 2018) organized
through an arranged cooperation with the second author’s ecology support and evaluation
focused NGO CooLAND (CooLAND, 2016a, 2016b) the first ecological pre-study of the
locality (Zímová, 2016). This pre-study served for reasoning of the eco-systemic support
envisioned community project’s relevance. And it was used to start building on the project and
for submitting a detailed investigation proposal for funding.
In the spring semester of 2017, the fully transdisciplinary systems oriented co-design
project began among the Faculty of Art and Architecture at TU of Liberec Faculty of Forestry
and Wood Sciences, the local community and the local environment, with the leadership by
Collaborative Collective and CooLAND (see Figure 2). This ‘GIGA-mapping’ (Sevaldson,
2011, 2015) and ‘full scale realisation prototyping studio’ (Davidová & Sevaldson, 2016)
focuses on supporting the local bio-tope by building shelters for the habitats of bats, insects,
homeless people, etc. The design process, prototyping and further local development fully
engage the local specific environment5 along with the local community. In this sense, it not
only involves participation but also co-design6. The co-design method involves both biotic and
abiotic performative agency within a so-called ‘Time Based Design’. Time-based Design was
investigated by Sevaldson, focusing at that the project does not end by the building finalisation
(Sevaldson, 2004, 2005, 2017b). This paper describes the first steps in this research-design
process.
Figure 2. An action diagram showing the integration of the Local Community, NGOs, Academy and
Sponsors for Future Co-Design and Co-Living (Davidová 2017).
The project aim is to motivate humans to co-live within the eco-system with other species and
with each other across social differences. Massey points out that an aspect of the
universalisation of the meaningfulness of place ironically concerns the production of difference.
She also states that such struggles over place, and the meaningfulness in and of place, to the
argument that in any even minimal recognition of the relational construction of space and of
identity, ‘place’ must be a site of negotiation, which will often be a conflictual negotiation
(Massey, 2004). The common events, such as prototype installations or seed bombs, topicrelated lectures and workshops, cultural performances and bat mapping, at the EnviroCity
festival (Davidová & Kernová, 2016) did not avoid such problematique. On the contrary, they
prompted the discussion. The aim to support the eco-system7 through eco-systemic
‘prototypical urban interventions’ provoked an unavoidable discussion directly on site due to
their generative character, attaining a high impact through small input (Davidová, 2004;
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Doherty, 2005); however, none of this was done in an aggressive manner. The strength of the
project lies within the search for a balanced, systemic, co-living, real-life performance across
stakeholders with highly different interests.
Therefore, due to this bottom up (in combination with top down) approach to the
project’s performance and its discussions and publication, in less than one year, a new owner
bought the property from the one that claimed to have insufficient finances to preserve the
precious garden and the log house, thus arguing for commercial development. The new owner
claimed it would be refurbished into a new retreat centre for both humans and the biotope. The
announcement promises that a health centre that offers psychological, wellness, yoga and other
healing services will be built within the log house and that strong, true eco-systemic services
for all will be offered within its garden. Similar to the COLridor’s project program, it promises
bat houses, insect hotels, blossoming gardens, etc., and most importantly, a co-living
environment for all.
A similar understanding of cross-species co-living has been presented by feminist
Science and Technology Studies (STS) based on the concept of ‘caring’ in reference to other
species in which different territorial needs and understandings play crucial roles within
togetherness (Metzger, 2014); however, the notion of ‘caring’, regardless of the complexity of
the context it covers (Sevenhuijsen, 1998), appears to operate from a superior perspective as
opposed to the discussed co-living and co-design (eco-) systemic performance conditions. This
one involves culture, the social environment, habitation and the ‘edible landscape’ because
urban wildlife is critical to ecosystems (Adams & Lindsey, 2016; Creasy, 2004). Therefore, the
aim is to reinterpret and/or to extend and to rethink the commonly perceived mission of
architecture and urban design.
Figure 3. The GIGA-Map involves mapping the architectural performance, graduating the first author’s
authored and co-authored projects from fully open to almost closed and relating the eco-systemic
agency that passes their boundary conditions in feedback loops. The performance was evaluated based
on the conclusion that the more trans-agency performance interacting across architectures, the more
benefits to human agents (Davidová, 2016b).
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Considering the overall agency across the eco-system, this (eco-)systemic ‘nonanthropocentric architecture’ (Hensel, 2013, 2015) was concluded by the first author’s
previous study on performance to also be the most beneficial to humans. These benefits are
generated through its performance, its opportunities of use and its sustainability (Davidová,
2016b) (see Figure 3), including opportunities for food, climate comfort, dwelling, intimacy,
resting, social interaction and personal as well as common experiences.
Systemic approach to architectural performance methodology driven design field in the
COLridor project
While performing Research by Design during full-scale prototyping, the first author developed
her own design field. The Systemic Approach to Architectural Performance (SAAP) was
ratified in January 2017 as a fusion of process‐based fields formally initiated by the integration
of ‘Systems Oriented Design’ methodology (Sevaldson, 2012, 2013, 2017b) and ‘Performance
Oriented Architecture’ (Hensel, 2011, 2012, 2013). The approach allows for developing
methodology and generating theory through experimental practice. SAAP involves Time Based
Eco‐Systemic Co‐Design, which is performed through both biotic and abiotic agency, including
human agents. It belongs to a broader field of Systemic Design while considering the overall
eco-system in action. Here, it was achieved through the engagement of eco-systemic
‘prototypical urban interventions’ (Doherty, 2005) in public space and thus through
interactions with and integration within the (eco)system. The (eco)system is hence co-designed
and re-designed along with all interacting agencies involved. As demonstrated, this co-design
consists of an efficient mixture and fusion of several types of co-performative processes.
Trans-disciplinary and public based co-design
As mentioned, the project was developed based on an ecological pre-study of the location.
Furthermore, community and invited experts attended GIGA-Mapping co-design workshops at
a local restaurant. During these workshops, the design and realisation of eco-systemic
prototypical urban interventions were co-developed in the forms of an insect hotel, called
TreeHugger and various public intervening events of the EnviroCity 2017 Festival, whichagain,
included the GIGA-Mapping workshop by invited lecturers to enrich the processes. The GIGAMaps were exhibited on-site for the community to interact with them. Following the
application, while receiving attention from a variety of communities, the TreeHugger
responsive wood insect hotel model code was placed online as an open source, acting as a
Christ-Mass present available to communities anywhere in the world. Therefore, the project
aim is aleso to reach local communities and ecologies globally.
GIGA-mapping workshops
Following a series of lectures from each of the specialist team members and a study field trip,
the team arranged an initial GIGA-mapping workshop. Though on-site, the first workshop was
arranged in an exclusive (not inclusive) setting. Each of the team members, who were from
different disciplines, GIGA-mapped their individual field’s interests and speculations within
the project to search for intersections (see Figure 4). This mapping helped co-organise
individual interests to initiate teamwork. Therefore, this event was crucial despite the fact that
some of the original members decided to discontinue participation in the project because it did
not meet their expectations or required a significantly larger workload than originally expected.
While establishing the aims, each participant was asked to print reference pictures of the items
they wanted to discuss for the next GIGA-Mapping workshop that was already public. The use
of images during GIGA-Mapping also brings tacit, even sub-conscious, layers into play
(Davidová, 2016b, 2016d, 2017d; Davidová & Uygan, 2017) and therefore better stimulates
Shön’s ‘reflection in action’ (Schön, 1983) during the design process. This is because the
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GIGA-Map has several more dimensions as well as relations within these dimensions. The
workshop focused on searching for such, utilising drawing techniques (see Figure 5). The
follow-up workshops utilised the gathered images and drawing information and implemented
them into multi-layering on preprints (see Figure 6 and Figure 7).
Figure 4. 1st GIGA-Mapping Workshop for the COLridor Project. In this case, this is an image of the
Trans-Disciplinary Experts’ Collective Mind Mapping (photo: Davidová 2017).
Figure 5. 2nd GIGA-Mapping Workshop for COLridor Project - combination of drawing and printed
images correlating (photo: Davidová 2017).
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Figure 6. Photograph taken shortly after the beginning of the third workshop (photo: Davidová 2017).
Figure 7. A detailed pre-printed map after the workshop that shows the timeframe planning of
EnviroCity’s events as well as the Eco-Systemic Performances (photo: Davidová 2017)
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Figure 8. Speculative GIGA-Map relating the stakeholders’ feedback looping the interactions within
EnviroCity’s actions and the scale of the locality they relate to (Davidová, 2017c) – Please see the
reference for a preview of the full .pdf file.
The mapping for the interventions resulted in the concept design of the EnviroCity festival
events and the insect hotel design for prototyping, both of which are discussed later in this
article. The stakeholders with an interest in building development did not join the project;
however, they actively followed it, and within the GIGA-Mapping processes, it was attempted
to represent them through interpretations of their interests. All the gathered speculations on ecosystemic relations among stakeholders (including our team as well as local species), their aims
and the designed interventions were digitally GIGA-Mapped and updated over time by the first
author and were useful in understanding and leading the project (see Figure 8). The final map
is relating the stakeholders’ city scale activity areas and types, their interests and their
preferences (see Figure 9 and Figure 10) as well as feedback looping among them related to the
planned actions and activities (see Figure 11, Figure 12 and Figure 13). The relations were
collectively mapped and speculated across the disciplines, the community and its political
representations.
Figure 9. COLridor GIGA-Map's in detail that shows the stakeholders’ city scale relations and interests
and preferences in relation to the project. The stakeholders include those from the municipality, local
authorities, local or engaged organisations and types of local residents. Please see the following figure
with anoter detail to review the full list (Davidová 2017).
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Figure 10. COLridor GIGA-Map's in detail that shows the stakeholders’ city scale relations and interests
and preferences in relation to the project. The stakeholders include from the municipality, local
authorities, local or engaged organisations and types of local residents. Please see the above figure
with another detail to review the full list (Davidová 2017).
Figure 11. COLridor GIGA-Map in detail that shows some of the feedback looping related to the
COLridor’s and the EnviroCity’s actions and activities within the project stakeholders’ agency – please,
see the following figures to review the full list (Davidová 2017).
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Figure 12. COLridor GIGA-Map in detail that shows some of the feedback looping related to the
COLridor’s and the EnviroCity’s actions and activities within the project stakeholders’ agency– please,
see the above and below figures to review the full list (Davidová 2017).
Figure 13. COLridor GIGA-Map in detail that shows some of the feedback looping related to the
COLridor’s and the EnviroCity’s actions and activities within the project stakeholders’ agency – please,
see the above figures to review the full list (Davidová 2017).
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The GIGA-map is still publicly exhibited in the garden of the restaurant. It performed as a
discussion board during the EnviroCity festival, which is also discussed in the subsequent
section. All attending stakeholders were interested in locating themselves on the map and
following and discussing their relations to others. The analysis of relations also served as a tool
for interactions and expectations as well as the branding of the events and actions. Therefore, it
could be stated that the GIGA-Map is also an eco-systemic urban intervention that engages and
generates the public co-design of the project.
EnviroCity Festival prototypes
The concept of the multi-genre EnviroCity Festival (Davidová & Kernová, 2016) is very open,
though there is one strict rule: all performers (dancers, performing artists, AV artists, musicians,
lecturers, workshops leaders, disputers, etc.) must have been somewhat related to the topic of
the project. Therefore, the trans-disciplinary performers co-designed the project through their
performance, the project’s interpretation (Davidová, 2017d) and their influence on the
audience. The fields consisted of local community ecological NGOs (see Figure 15), politicians
(see Figure 14), social-geographers, architects (see Figure 19), national heritage architects (see
Figure 14), systemic designers (see Figure 17), ecologists (see Figure 18) and biologists as well
as dancers and performing artists (see Figure 16) and audio-visual shows (see Figure 20). Some
performances were more interactive and some less, and some were either more or less researchoriented. Therefore, a broad range of ages and social groups became engaged and participated
in the festival events. Even the owner, whose interests were related to development, observed
the events through his window and often participated on-place, though not actively.
While the discussions among politicians and experts helped reach some solutions at the
public agencies level, the artistic performances and ecological workshops, such as seed bombs
and bird and bat mapping, included the audience through personal but public engagement. The
research-oriented lectures engaged a more professional community in the research field. In
addition, the knowledge generated through these performances had diverse characteristics.
While researchers tend to provide in-depth explicit references, proposals regarding how to
approach the issues and discussions, performing artists tend to communicate on tacit or even
subliminal levels (see Figure 16 and Figure 20), all mainly relating to urbanised ground and/or
its options for social situations. The NGO’s brunch (see Figure 15), the community GIGAMapping workshop (see Figure 17), the interactive AV, AR and VR games for children (see
Figure 19) and the political discussions (see Figure 14) allowed for exchanging specific local
information and generated a sense of community togetherness. The physical seed bombing (see
Figure 21) and the various types of species mapping (see Figure 18) offered learning through
interaction, while Systems Oriented Design, environmental design, social geography and
traditional architecture eco-systemic performative capacities references were also discussed.
Although these prototypes often had no physical character, they all served as prototypical urban
interventions, generating eco-systemic performance through co-design, whether through public
or other means (seed bombs, etc.).
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Figure 14. Debate on Bio-Corridors within the city and their relation to Bio-Top Zvonařka – the disputers
consisted of a National Heritage Architect, City Hall Representative for Urban Development, Prague 2
District Counsel, the first author as an Architect and the second author as an Ecologist. The discussion
had a stated goal to discover common strategies for action (photo: Robert Carrithers 2017).
Figure 15. Community brunch discussing Initiatives for Eco-Systemic Co-Living (photo: Robert
Carrithers 2017).
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Figure 16. Darina Alster: Sea Siren, Costume design: Darina Alster & Václava Davidová (Photo: Robert
Carrithers 2017).
Figure 17. Who We Are / Who Are We’ Community GIGA-mapping workshop by Linda Blaasvær (Photo:
Robert Carrithers 2017).
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Figure 18. Morning picnic with birds – Local Bird Mapping performed by Kateřina Zímová (photo: Robert
Carrithers 2017).
Figure 19. VR game Bumblerun by Kateřina Horák Goryczka and Jan Horák in the public space of Nusle
Stairs (photo: Robert Carrithers 2017).
Figure 20. Lunchmeat Eco-Systemic Closing Audio-Visual Performance (photo: Go 2017).
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Eco-Systemic Urban Prototypical Interventions
The eco-systemic urban prototypical interventions inspired by CHORA’s ‘urban prototypical
interventions’ (Doherty, 2005) can serve as an input stimuli for an eco-system to begin
flourishing. For the COLridor project (Davidová, 2017b) with its festival EnviroCity (Davidová
& Kernová, 2016), three interventions that were interlinked were categorised:
Edible Landscape
The project promotes the concept of an ‘edible landscape’ (Creasy, 2004). For an eco-top to
flourish, above all, there must be enough food. As birds and bats are crucial species to the
location, an insect hotel was built (see Figure 22) to provide their food; however, this impending
food must also be nourished, and there has been a nearly 80% decrease in flying insects since
the 1980s in Western and Central Europe (Vogel, 2017). The situation for birds in Czech
agricultural lands is similar (Czech Ornithologists Association, 2016b). Therefore, EnviroCity
implemented a Seed Bombing workshop with blossoming flowers to offer honey (see Figure
21) for insects as well as fruits and seeds for birds. While doing so, this increase in the greenery
surface intervention also addresses an ‘urban heat island problematique’ (Wong, Hogan,
Rosenberg, & Denny, 2016), thus supporting habitable and liveable environmental conditions
that generate a richer edible landscape.
Figure 21. SeedBombs Workshop by Kateřina Zímová (photo: Robert Carrithers 2017).
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Habitation
The first prototype for habitation is the insect hotel TreeHugger (see Figure 22). The hotel
employs the concept of responsive, solid wood from Norwegian traditional architecture. This
concept involves the tangential section through the tree trunk, and thus the fibre density on the
left and right sides of the plank is different. Therefore, the plank warps in low relative humidity
and high temperatures, while in humid, cold weather, it is narrow. When organised into a screen,
the system airs in dry weather and closes in humid weather (Larsen & Marstein, 2000).
Figure 22. TreeHugger: Responsive Wood Insect Hotel that offers a variety of climatic and spatial
conditions to be met with diverse insects’ preferences. This is achieved by global axis orientation, the
shape of the hotel and cutting the panels from different positions of the tree trunk. Please also take note
of the social communication and engagement between people and the insect habitation architecture
(photo: Robert Carrithers, 2017).
Figure 23. Ray 2 Responsive Wood Envelope Prototype: a) in semi-dry April weather when the screen
is partly open for a boundary exchange between the exterior and the semi interior; b) After a light rain
in April when the System is closed to prevent the humid and cold air from passing through the boundary;
both after four years of exposure to weather and biotic conditions. The prototype became inhabited by
Blue Stein Fungi, Algae and Lichen. These, especially the algae, regulate the moisture content of the
wood, thus contributing to its warping. Notice also the organisation of the Algae habitation caused by
the material’s fibre direction and position within the design, which is affected by material performance
and form. Thus, it is organised through its moisture and the organisms’ abundance and distribution
interaction (photo: Davidová 2017) (Davidová, 2017a).
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Figure 24. The internal chambers of TreeHugger, which offers different climatic zones (photo: Davidová
2017).
This prototype is a further development of the first author’s responsive wood screen Ray
(Davidová, 2014b, 2014a, 2016a, 2017a) (see Figure 23) in which the warping is moderated
based on the moisture content when the wood is cut. Certain positions within the tree trunk
cause the differences in warping. The difference in warping not only enables the organisation
of the panels’ overlapping but also generates diverse climatic habitation chambers within the
hotel (see Figure 24). Therefore, the hotel caters to a large diversity of insects and other species
that are also supported by the terrain and world axis orientation. This wooden platform offers
dwellings for algae, which also moderate its performance through moisture content (Davidová,
2017a, 2017d). Both the wood and the algae, performing together, also generate microclimatic
performance (see Figure 25). By sorping8 the moisture at night when the relative humidity is
high and by evaporating it on hot and dry summer afternoons, this intervention addresses an
‘urban heat island problematique’ (Wong et al., 2016), thus supporting habitable and liveable
environment conditions. This insect hotel also serves as a fast –food restaurant for birds and
bats. Therefore, the first responsive wood dwelling supports the bio-chain top down for
pollination as well as bottom up for birds and bats.
Figure 25. TreeHugger inhabited by algae and other species after the winter. It is apparent that the
prototype offers a material-climate performance, providing opportunities for dwellings for several species
of fauna and flora (Davidová 2018).
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Social interaction
Social interaction potentially has the most crucial impact on the ecosystem. Without public
engagement, our mission will stagnate and cannot develop into the concept of sustainability,
defined by Ehrenfeld as the possibility that humans and other life will flourish on the Earth
‘forever’ (Ehrenfeld & Hoffman, 2013). This impact through interaction was specifically
increased through the EnviroCity festival discussed above. After receiving local as well as
global public attention, open access to the TreeHugger Grasshopper 9 model code was made
available to download online on the Systemic Approach to Architectural Performance page
(Davidová, 2016c) and shared the link with network. The project and its code can be adapted
to local specific settings during workshops and through online recipes in other locations, such
as in Prague or Cyprus, to exhibit the adaptation. This strategy of spreading a tested prototype
through DIY10 when the public space is tagged through QR codes leading to the link to the
manual and Grasshopper codes. This approach for spreading the applications proved to be the
most efficient strategy for advancing the projects across communities to the first author: We
could exemplify the project ‘One More Tree’ on communities growing trees in public space
‘how to do manual’ (Sidorová et al., 2013) or ‘The Love to Landscape Proceeds through
Stomach’ sustainable farming support by city communities project organisation (Janovská,
Zímová, Krčíková, Wranová, & Valeška, 2016). With this approach, the authors might reach
somewhat of the ‘butterfly effect’1 through their social intervention initiation.
Eco-Systemic Performance Registrations and Observations
While performing all above, the time-based registrations and observations were tracked over
time, beginning with the project’s initiation and continuing to the present. This approach to
‘learning by doing’ 11 initiates Shön’s ‘reflection in action’ (Schön, 1983), and during these
performative processes, it therefore co-evolves into the ‘Time-Based Design’ (Sevaldson, 2004,
2005). Based on the observations, the complexity of the greenery consists of a mosaic of urban
greenery, permanent grasslands, private gardens and ruderal stands along the railway line. The
greenery is a varied species composition representing all floors from trees to herbaceous plants.
Some trees have significant ecological importance due to their ages and habitats, especially
trees in the private gardens on the streets Pod Zvonařkou and Na Klenovce. The complex
greenery area is located on a sloping terrain; the entire site slopes down to the Botič stream and
railway lines. The Zvonařka greenery complex, based on observations, is an ecological enclave
in the middle of an urbanised environment. The site is ecologically valuable for several different
reasons:
• The area is an important breeding and food biotope for birds and bats.
• The area is valuable due to its species diversity and the occurrence of nectar plants for
pollinators, which are currently included among the highly vulnerable groups with a priority
for protection according to the European Commission (European Commission, 2015).
• The location of the greenery area on a distinctive slope has a unique anti-erosion function,
thus protecting lower-lying sites that are heavily urbanised.
• Greenery plays a positive role in the microclimate of the site, thus avoiding the temperature
extremes typical within an urban environment.
• The site is the only corridor for species migration between adjacent systems of urban greenery.
• For Havlickovy and Folimanka Parks, these greenery systems have no other migration
potential due to the heavily urbanised environment surrounding them.
• The area is crossed by the NRBK 40 bio-corridor.
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• It is part of the concept of flood protection of MoE No. 11 - PPO Complex in the Lower Vltava
River Basin in the section Štěchovice - Mělník, meaning the action Botič Revitalisation is
covered. Due to its rich patricity, biomass concentration and slope location, the site has
significant hydrological importance for water retention in the countryside and for protection
from local flooding.
Biological Observations
A field survey was conducted from April 2017 to October 2017. During this survey, the entire
site was explored in terms of functional ecological links outside the site and its interaction with
the surrounding greenery. The collected field data were then compared with information from
professional sources (AOPK, 2017) and subjected to an overall evaluation. Among the species
identified, a total of 27 more common bird species and two more common listed bat species
were observed (see Figure 26), and it was registered that they have no safe opportunities for
nesting. Burnt nested bats were found in the baskets inside the heating exits of human dwellings.
These observations can serve as a source for the next prototyping initiation. From the beginning
of the project and the time of TreeHugger placement to the beginning of autumn, its slow
inhabitation was recorded. It is currently assumed to be used by butterflies for overwintering,
and this assumption can be tested in the spring when new seed-bombing is necessary. The
increase in the larger eco-systemic chain is subject to long time span observations. These
observations will be used to inform the project process and will be interpreted through
upcoming GIGA-Mappings and eco-systemic urban intervention prototypes.
Figure 26. A sample from the Ultra Sound Bat Detector Recording registering two species of bats from
the location (Bat Protection Association 2017).
Birds species registering (see Figure 18)
Contrary to exceptions, few rare species were observed; however, the site studies indicated the
potential for the habitation growth and its landscape adaptation, which would provide a larger
amount and range of nutrient and nesting opportunities that could change the situation, although
determining this would require annual registering over a large time span.
Based on the observation on 31st May 2017, the following species were registered:
Phylloscopus collybita (see Figure 27), Phylloscopus trochilus, Turdus philomelos,
Turdus pilaris, Columba palumbus, Delichon urbica (see Figure 28), Motacilla alba,
Turdus merula, Sylvia atricapilla, Sylvia curruca, Sylvia communis, Fringilla coelebs,
Falco tinnunculus, Phoenicurus ochruros, Garrulus glandarius, Carduelis carduelis, Pica
pica, Dendrocopos major, Dendrocopos minor, Emberiza citronella, Troglodytes
troglodytes, Parus major, Parus caeruleus, Sturnus vulgaris, Corvus corone, Carduelis
chloris (see Figure 29) and Picus viridis.
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Figure 27. Phylloscopus Collybita, which is a small singing bird that inhabits an area ranging from
Western Europe to Siberia. It is mainly a migrating bird that originally nests in mixed forests with dense
shrubs; however, recently, it has often been registered in green urban areas. While clearing pollution in
Czech cities, its slight increase was recently registered (Czech Ornithologists Association, 2016a). It
subsists on mainly insects. The photo is used with a creative commons licence from (Trepte, 2013).
Figure 28. Delichon Urbica babies nested in an urban settlement. These are small birds in an area
ranging across Eurasia. Originally, they preferred open land with low vegetation, which usually includes
pastures, meadows and farmland, preferably near water areas. Recently, they more often inhabit and
nest in colonies in urban areas, as seen in the picture. They subsist on insects. The photo is used with
a creative commons licence (Ableiter, 2007).
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Figure 29. Carduelis Chloris is a singing bird that inhabits mostly cultural landscapes of almost all of
Europe except some parts of Scandinavia, Great Britain and Island. The population from the northern
regions migrates. It subsists on seeds and insects. In Czechia, the population has extensively decreased
since the year 2010 (Czech Ornithologists Association, 2016a). The photo is used with a creative
commons licence (Thermos, 2006).
Bat species registering (see Figure 26)
The bat ultrasound registering tool captured signals of Pipistrellus pipistrellus (see Figure 30)
and Pipistrellus nathusii (see Figure 31) on 14th May 2017. These are not the rarest local
species; however, all Czech local bat species are protected and listed as endangered. Based on
a more extensive area registration, it was concluded that these species use the particular
location for hunting, not for nesting. They nest in larger parks on the discussed bio-corridor,
and unfortunately, they often attempt to nest in the heating exits of urban areas in
neighbourhoods. The lack of nesting opportunities leads to decreases in entire communities
when the heating season begins. Therefore, the local bat monitoring report proposes to
support a nesting and nutrient increase in this ecologically crucial locality (Zieglerová, 2017)
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Figure 30. Pipistrellus pipistrellus is most likely the most common type of bat species in Czechia and
Central Europe. Its habitat ranges from almost everywhere in Europe except the northern regions of
Kashmir and Altaj. It requires either low or lower lands. It overwinters in caves or cellars, and in the
summer, it nests in buildings and roof cavities. It lives in communities and subsists on insects. The photo
is used with a creative commons licence (de Longe, 2005).
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Figure 31. Pipistrellus nathusii is a migrating bat whose habitats range from Western Europe to
Caucasus and Turkey. Of these regions, it is most common in Central Europe. It nests mainly in forests,
and as its Czech name suggests, frequently in parks, both near water sources. It subsists on insects.
The photo is used with a creative commons licence (Mnolf, 2006).
Summary
This case study demonstrates that the methodology and the ‘project’s result’ can be fused
together within an ongoing time-based, real time, co-design performance. This involves both
biotic and abiotic agency across the local specific eco-system, which acts in equal roles. The
project combines the bottom up and the top down approaches for the generation of an edible,
social, cultural and habitable urban environment across species and for the overall eco-systemic
agency to reach a ‘flourishing for all’ (Ehrenfeld & Hoffman, 2013) state. In other words, the
project discuss life, generating the situations to address several parameters:a) live (socially,
culturally, etc.), b) dwell (climate comfort, etc.), c) eat and d) be eaten; flourishing eco-system
across species performing together. A wild party, to say…The case study included multilayered co-design approaches involving human and non-human actors and representatives
within the initial and the performance co-design processes. All data are currently being
registered, reflected and reused in forthcoming co-design processes. Therefore, as the project’s
GIGA-Map shows, all its relations, interactions and evolutions occur due to rather complex,
generative, time-based feedback loops.
Discussion and Conclusions
To ensure that ecological and various other site functions mentioned are preserved, it is
necessary to keep the current green areas in the current state, November 2017. The site has the
potential to provide a biotope for the observed common or rare or even protected species, such
as bats, birds and insects. It is crucial that the site provides food and dwellings for them to
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survive, especially because many are only adapted to living in an urban environment and
because agricultural land is often even less conducive to their chances to survive.
Another problematique the project addressed by increasing biodiversity and blossoming green
surfaces through social action is the urban heat island. Meineke, Dunn, Sexton and Frank
(Meineke, Dunn, Sexton, & Frank, 2013) stated that heat can be a key driver of insect pest
outbreaks in urban trees. Heat islands in cities could therefore be detrimental not only to climate
change but also to biodiversity and vice versa. Thus, it is important to continue the observations
and research of the diversity of pollinators and other insects, birds and bats that rely on them as
well as blossoming plants in cities and to support those that are endangered or rare. Knop
pointed out that urbanisation could have a negative impact on rare and specialist species (Knop,
2016). These species, along with others, are also disappearing from agricultural land due to
pests, herbicides, etc. There are few types of land remaining in Central Europe other than
mountain areas, and not all species have adapted to these areas. Specific solutions, such as
COLridor, supporting specialist species that are typical for the biogeographic region through
eco-systemic urban interventions could help increase local specific biodiversity. As local
species begin to adapt to cities, the cities must adapt to this co-living situation as well to prevent
an even larger biodiversity loss.
The project clearly requires larger and longer time span observations and interventions;
however, it is already clear that to achieve the proposed objectives, it is necessary to involve
both bio-technological research as well as the local human community in the vision to co-design
the urban environment and to cohesively inhabit it along with other species. The media mix of
both GIGA-Mapping and prototypical actions adapted to momentary research investigations
appear to be effective design-research tools. Their performance should be perceived as both the
design process and the ‘over-evolving’ design results-prototypes within the eco-systemic codesign and re-design performance for co-living situations in urban environments. Therefore, it
is claimed that designing with- rather than designing for- should be performed. It is alarming
that the UN agenda for 2030 sustainable development is calling for a collaborative partnership
between all stakeholders to eradicate poverty while determining to ensure that economic, social
and technological progress occurs in harmony with nature to reach prosperity (United Nations,
2015); however, its goals are so anthropocentric that ‘Cities and Communities’ are discussed as
a separate goal (United Nations, 2015, 2016a) from bio-diversity and are discussed in relation
to the ‘Life on Land’ goal (United Nations, 2015, 2016b). These goals are not in any sense
cross-referenced. As opposed to this human-centred approach, this project demonstrates the
relevance of considering human settlements as part of and taking part in the overall eco-system.
Based on this small case study, it is apparent that it is not possible to achieve social justice
without environmental justice and vice versa. This is because humans play full and equal—
neither privileged nor pejorative—roles within the overall eco-system and biosphere. This fact
cannot be neglected to shift from Anthropocene towards the sustainable co-living futures of
Ehrendfeld’s ‘flourishing for all’ (Ehrenfeld & Hoffman, 2013).
Through the generation of public awareness and pride for the local specificity and
community, the bio-corridor can be marked into the metropolitan plan, and no future building
development in the precious garden would be permitted. At the same time, the aim is to achieve
a broader impact on other communities around the world by spreading awareness of the project
through social media using a DIY strategy that should be adapted to the local eco-systemic,
including natural, social and cultural environmental settings, by its appliers. Through this multilayered ‘Ecological Urbanism’ that involves ‘anticipation, sensing, curation, collaboration,
production, interaction, mobilisation, measures, adaptation and incubation’ (Mostafavi &
Doherty, 2016b, 2016a), our policies are targeted to be implemented from the bottom up. The
fusion of the discussed eco-systemic co-design performances and the processes involved in co-
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Marie Davidová and Kateřina Zímová COLridor
living justify the relevance of the recent ratification of the Systemic Approach to Architectural
Performance design field.
Acknowledgements
The project is co-organised by Collaborative Collective, z.s., CooLAND,
z.s. with the support of the Technical University of Liberec, Faculty of
Art and Architecture and the Faculty of Forestry and Wood Sciences at
the Czech University of Life Sciences in Prague and was co-designed
with them, respectively, along with the local community and the local
environment. It has been co-funded by the VIA Foundation and through
an EEA Grant program for Biodiversity and Climate Change Adaptation
led in cooperation with the Technical University of Liberec, Faculty of
Art and Architecture and the Oslo School of Architecture and Design.
The sponsorship involved the Forests of the Czech Republic, Stora
Enso, Rothoblaas, Škuta Design and the Faculty of Forestry and Wood
Sciences at the Czech University of Life Sciences in Prague. The
festival events were listed as a part of European Sustainable
Development Week and European Cultural Heritage Days.
Marie Davidová
Architect and Researcher, MArch, Ph.D.
Collaborative Collective, z.s. (chair)
Welsh School of Architecture
md@collcoll.cc
Kateřina Zímová
Landscape Ecologist and Researcher, ing.
Collaborative Collective, z.s.
CooLAND, z.s. (chair)
kz@collcoll.cc
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References
Ableiter, C. (2007). Zwei Jungschwalben im Nest. Retrieved March 8, 2018, from
https://commons.wikimedia.org/wiki/File:Zwei_Jungschwalben_im_Nest.jpg
Adams, C. E., & Lindsey, K. J. (2016). Urban Wildlife Management (2nd ed., Vol. 109). Boca Raton: Taylor &
Francis Group. https://doi.org/10.1017/CBO9781107415324.004
Allen, T. F. H., & Roberts, D. W. (1993). Foreword. In R. E. Ulanowicz (Ed.), Ecology, the Ascendent
Perspective (pp. xi–xiii). New York: Columbia University Press.
Begon, M., Harper, J. L., & Townsend, C. R. (2006). Ecology: Individuals, Populations and Communities.
Blackwell science (4th ed., Vol. 1). Malden-Oxford-Carlton: Blackwell Publishing Ltd.
https://doi.org/10.1007/s13398-014-0173-7.2
Boeing, G. (2016). Visual Analysis of Nonlinear Dynamical Systems: Chaos, Fractals, Self-Similarity and the
Limits of Prediction. Systems, 4(4), 37. https://doi.org/10.3390/systems4040037
Collaborative Collective. (2012). Collaborative Collective. Retrieved January 1, 2013, from
http://www.collaborativecollective.cc/
Collaborative Collective. (2016). Coll Coll. Retrieved August 14, 2016, from
https://www.facebook.com/collaborativecollective/
CooLAND. (2016a). CooLAND. Retrieved August 24, 2016, from http://www.cooland.cz/
CooLAND. (2016b). CooLAND. Retrieved August 24, 2016, from https://www.facebook.com/cestadokrajiny/
Creasy, R. (2004). Edible Landscaping. Gainesville.
Czech Ornithologists Association. (2016a). Jednotný program sčítání ptáků: Indexy a trendy 2016 / The
Individual Progarm of Birds Accountinf: Indexes and Trends in 2016. Prague: Česká společnost
ornitologická / Czech Ornithologists Association. Retrieved from
http://jpsp.birds.cz/vysledky.php?taxon=864
Czech Ornithologists Association. (2016b). The Annual Report of the Czech Ornithologists Association / Výroční
zpráva České společnosti ornitologické 2016 birdlife.cz. Prague. Retrieved from
http://bigfiles.birdlife.cz/Vyrocni_zprava_CSO_2016.pdf
Davidová, M. (2004). Gary Doherty: On Spatial Dialogues. Stavba, 5(6), 18.
Davidová, M. (2014a). Ray 2: The Material Performance of a Solid Wood Based Screen. In E. Thompson (Ed.),
Fusion - Proceedings of the 32nd eCAADe Conference - Volume 2 (Vol. 2, pp. 153–158). Newcastle upon
Tyne: Faculty of Engineering and Environment, Newcastle upon Tyne. Retrieved from
http://papers.cumincad.org/cgi-bin/works/paper/ecaade2014_011
Davidová, M. (2014b). Wood’s Material Performance: Ray2. In R. Cielatkowska & D. Jankovska (Eds.),
Wooden architecture, tradition, heritage, present, future – Proceedings1 (pp. 93–99). Gdansk: Wydział
Architektury Politechniki Gdańskiej za zgodą Dziekana. Retrieved from
https://www.researchgate.net/publication/307959365_Wood%27s_Material_Performance_Ray_2
Davidová, M. (2016a). Ray 3: The Performative Envelope. In M. S. Uddin & M. Sahin (Eds.), 2016 DCA
European Conference: Inclusiveness in Design (pp. 519–525). Istanbul: Özyeğin University. Retrieved
from https://www.researchgate.net/publication/307934969_Ray_3_The_Performative_Envelope
Davidová, M. (2016b). Socio-Environmental Relations of Non-Discrete Spaces and Architectures: Systemic
Approach to Performative Wood. In P. Jones (Ed.), Relating Systems Thinking and Design 2016
Symposium Proceedings (pp. 1–17). Toronto: Systemic Design Research Network. Retrieved from
https://www.researchgate.net/publication/312501181_Socio-Environmental_Relations_of_NonDiscrete_Spaces_and_Architectures_Systemic_Approach_to_Performative_Wood
Davidová, M. (2016c). Systemic Approach to Architectural Performance. Retrieved March 29, 2016, from
https://systemicapproachtoarchitecturalperformance.wordpress.com/
www.FormAkademisk.org
26
Vol.11 Nr.4 2018, Art. 5, 1-30
Marie Davidová and Kateřina Zímová COLridor
Davidová, M. (2016d). Wood as a Primary Medium to Architectural Performance: A Case Study in Performance
Oriented Architecture Approached through Systems Oriented Design (1st ed.). Liberec: Technical
University of Liberec. Retrieved from
https://www.researchgate.net/publication/307957987_Wood_as_a_Primary_Medium_to_Architectural_Per
formance_A_Case_Study_in_Performance_Oriented_Architecture_Approached_through_Systems_Orient
ed_Design
Davidová, M. (2017a). Co-Habited, Co-Lived, Co-Designed and Co-Created Eco-Systemic Responsiveness in
Systemic Approach to Architectural Performance: A Case Study on Interaction of Performative Solid
Wood Envelope Ray and Algae. In M. João de Oliveira & F. Crespo Osório (Eds.), KINE[SIS]TEM: From
Nature to Architectural Matter (pp. 36–45). Lisbon: DINÂMIA’CET-IUL ISCTE - Instituto Universitário
de Lisboa. Retrieved from https://www.researchgate.net/publication/317819704_Co-Habited_CoLived_Co-Designed_and_Co-Created_EcoSystemic_Responsiveness_in_Systemic_Approach_to_Architectural_Performance_A_Case_Study_on_Int
eraction_of_Performative_Solid_Wood_Envelope_Ray_and_Alg
Davidová, M. (2017b). COLridor. Retrieved March 31, 2017, from https://www.facebook.com/COLridor/
Davidová, M. (2017c). COLridor GIGA-Map. In B. Sevaldson (Ed.), Relating Systems Thinking and Design 6:
Environment, Economy, Democracy: Flourishing Together (p. 1). Oslo: Systemic Design Research
Network. Retrieved from https://www.researchgate.net/publication/320558654_COLridor_GIGA-Map
Davidová, M. (2017d). Systemic Approach to Architectural Performance: The Media Mix in the Creative Design
Process. FORMakademisk, 10(1), 1–25. https://doi.org/10.7577/formakademisk.1713
Davidová, M., & Kernová, M. (2016). EnviroCity - Facebook. Retrieved April 1, 2016, from
https://www.facebook.com/envirocity/
Davidová, M., & Neshevets, N. (2018). Eco-Systemic Co-Design for DIY: Co-oCo-oNest, the Baby of
SpiralTreeHouse // Зозулине гніздо. Retrieved May 20, 2018, from
https://systemicapproachtoarchitecturalperformance.wordpress.com/2018/05/08/eco-systemic-co-designfor-diy-coocoonest-the-baby-of-spiraltreehouse-зозулине-гніздо/
Davidová, M., & Sevaldson, B. (2016). 1:1, A Transdisciplinary Prototyping Studio. In J. Slyk & L. Bazerra
(Eds.), ASK.the.Conference 2016 (pp. 302–308). Warszaw: Warszaw University of Technology, Faculty of
Architecture. Retrieved from
https://www.researchgate.net/publication/307935449_11_A_Transdisciplinary_Prototyping_Studio
Davidová, M., & Uygan, E. (2017). Living in Bio-Climatic Layers: An Investigation of Cappadocian Caves in
Relation to Today’s Design and Its Futures. In F. Mahbub, S. Uddin, & A. M. Khan (Eds.), International
Design Conference: DESIGN EVOLUTION [Education and Practice] (pp. 1–12). Karachi: Indus Valley
School of Art and Architecture. Retrieved from
https://www.researchgate.net/publication/313759290_Living_in_BioClimatic_Layers_An_Investigation_of_Cappadocian_Caves_in_Relation_to_Today%27s_Design_and_Its
_Futures
Davidová, M., & Zímová, K. (2017). COLridor: Co-Design and Co-Living for Sustainable Futures. In B.
Sevaldson (Ed.), Relating Systems Thinking and Design 6: Environment, Economy, Democracy:
Flourishing Together (pp. 1–20). Oslo: Systemic Design Research Network. Retrieved from
https://systemic-design.net/rsd6/systemic-design-cases/#davidova
Davidová, M. (2018). Collaborative Collective - research. Retrieved October 22, 2018, from
https://www.facebook.com/CollaborativeCollectiveResearch/
Davidson, S. (2017). Grasshopper - algorithmic modeling for Rhino. Retrieved October 6, 2017, from
http://www.grasshopper3d.com/
de Longe, J. (2005). Pipistrellus pipistrellus. Retrieved March 8, 2018, from
https://commons.wikimedia.org/wiki/File:Pipistrellus_pipistrellus01.jpg
Doherty, G. (2005). Prototypes in Pinkenba. In Nordes 2005 - In the Making (Vol. 1, pp. 1–5). Kopenhagen:
Royal Danish Academy of Fine Arts, School of Architecture. Retrieved from
http://www.nordes.org/opj/index.php/n13/article/view/262/245
www.FormAkademisk.org
27
Vol.11 Nr.4 2018, Art. 5, 1-30
Marie Davidová and Kateřina Zímová COLridor
Ehrenfeld, J., & Hoffman, A. J. (2013). Flourishing : a frank conversation about sustainability (1st ed.).
Stanford: Stanford University Press. Retrieved from
https://www.researchgate.net/publication/274250501_Flourishing_A_Frank_Conversation_on_Sustainabi
lity
European Commission. (2010). Green Infrastructure. Nature Environment. Brussel. Retrieved from
http://ec.europa.eu/environment/nature/info/pubs/docs/greeninfrastructure.pdf
European Commission. (2015). COMMISSION IMPLEMENTING REGULATION (EU) 2015/ 1368 - of 6
August 2015 - laying down rules for the application of Regulation (EU) No 1308/ 2013 of the European
Parliament and of the Council with regard to aid in the apiculture sector. Official Journal of the European
Union, 2015/1368(211), 9–16. Retrieved from http://eur-lex.europa.eu/legalcontent/EN/TXT/PDF/?uri=CELEX:32015R1368&from=CS
Hensel, M. (2011). Performance-oriented Architecture and the Spatial and Material Organisation Complex.
FORMakademisk, 4(1), 3–23. Retrieved from
https://journals.hioa.no/index.php/formakademisk/article/download/125/114
Hensel, M. (2012). Performance-oriented architecture: An integrated discourse and theoretical framework for
architectural design and sustainability towards non-discrete and non-anthropocentric architectures.
University of Reading. Retrieved from https://www.researchgate.net/publication/282856733_Performanceoriented_Architecture__An_integrated_discourse_and_theoretical_framework_for_architectural_design_and_sustainability_towar
ds_non-discrete_and_non-anthropocentric_architectures
Hensel, M. (2013). Performance-Oriented Architecture: Rethinking Architectural Design and the Built
Environment (1st ed.). West Sussex: John Willey & Sons Ltd.
Hensel, M. (2015). Performance-Oriented Design. Retrieved April 3, 2016, from
http://www.performanceorienteddesign.net/
Institute of Planning and Development Prague. (2016). Metropolitan Plan of Prague. Retrieved August 20, 2016,
from http://plan.iprpraha.cz/cs/upp-dokumentace
Janovská, V., Zímová, K., Krčíková, Š., Wranová, A., & Valeška, J. (2016). Láska ke krajině prochází žaludkem
/ The Love to Landscape Proceeds through Stomach. Prague: PRO-BIO LIGA. Retrieved from
https://www.researchgate.net/profile/Sarka_Krcilkova/publication/308414692_Laska_ke_krajine_prochazi
_zaludkem/links/57e3a50508ae054b20bcea2e/Laska-ke-krajine-prochazi-zaludkem.pdf
Knop, E. (2016). Biotic homogenization of three insect groups due to urbanization. Global Change Biology,
22(1), 228–236. https://doi.org/10.1111/gcb.13091
Kubeš, M., Janíčková, M., Koucký, R., Bohuniczky, A., Čermáková, M., Dvorská, N., … Fejfar, M. (2014).
Cesty zvířat: Územní systém ekologické stability jako základ rozmanitosti a prostupnosti krajiny - Animal
Paths: The Land System of Ecological Stability as a Basis of Landscape Diversity and Accesibility. In R.
Koucký (Ed.), Koncept odůvodnění metropolitního plánu - Concept of Metropolitan Plan Justification (1st
ed., pp. 0–28). Prague: Institute of Planning and Development Prague. Retrieved from
http://plan.iprpraha.cz/uploads/assets/booklet/500_cesty_zvirat_new/500_Cesty_zvirat_1str_rastr_ele_00.p
df
Larsen, K. E., & Marstein, N. (2000). Conservation of Historic Timber Structures: An Ecological Approach.
Oxford: Reed Educational and Professional Publishing Ltd.
Massey, D. (2004). Geographies of responsibility. Geografiska Annaler: Series B, Human Geography, 86(1), 5–
18. https://doi.org/10.1111/j.0435-3684.2004.00150.x
Meineke, E. K., Dunn, R. R., Sexton, J. O., & Frank, S. D. (2013). Urban Warming Drives Insect Pest
Abundance on Street Trees. PLoS ONE, 8(3), e59687. https://doi.org/10.1371/journal.pone.0059687
Metzger, J. (2014). Spatial planning and/as caring for more-than-human place. Environment and Planning A,
46(5), 1001–1011. https://doi.org/10.1068/a140086c
Metzger, J. (2017). Can the craft of planning be ecologized? (And why the answer to that question doesn’t
include ’ecosystem services’). In M. Kurath, M. Marskamp, J. Paulos, & J. Ruegg (Eds.), Relational
Planning: Tracing Artefacts, Agency and Practices (Vol. 2012, pp. 99–120). Cham: Palgrave Macmillan.
https://doi.org/10.1007/978-3-319-60462-6_5
www.FormAkademisk.org
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Vol.11 Nr.4 2018, Art. 5, 1-30
Marie Davidová and Kateřina Zímová COLridor
Mnolf. (2006). Pipistrellus nathusii. Retrieved March 8, 2018, from
https://commons.wikimedia.org/wiki/File:Pipistrellus_nathusii.jpg
Mostafavi, M., & Doherty, G. (2016a). Ecological Urbanism. (M. Mostafavi & G. Doherty, Eds.), Ecological
Urbanism (revised). Cambridge: Lars Müller Publishers. Retrieved from
https://www.academia.edu/25491739/Ecological_Urbanism_Revised_Edition
Mostafavi, M., & Doherty, G. (2016b). Ecological Urbanism in Latin America and Caribbean. URBE - Revista
Brasileira de Gestão Urbana, 8(1), 7–11. https://doi.org/10.1590/2175-3369.008.001.SE07
Oxford University Press. (2004). World Encyclopedia (1st ed.). Published Online: Philip’s.
https://doi.org/10.1093/acref/9780199546091.001.0001
Pegg, M. (2018). D is for John Dewey: His Approach To Education - The Positive Encourager. Retrieved
February 27, 2018, from https://www.thepositiveencourager.global/john-deweys-approach-to-doingpositive-work/
RH-Arch. (2011). Rezidential House Zvonarka. Retrieved August 20, 2016, from http://www.rharch.com/projekty/bytove-domy/bytovy-dum-zvonarka/bytove-domy
Sanders, E. B.-N., & Stappers, P. J. (2008). Co-creation and the new landscapes of design. CoDesign, 4(1), 5–18.
https://doi.org/10.1080/15710880701875068
Sandhu, H., & Wratten, S. (2013). Ecosystem Services in Farmland and Cities. In S. Wratten, H. Sandhu, R.
Cullen, & R. Costanza (Eds.), Ecosystem Services in Agricultural and Urban Landscapes (1st ed., pp. 3–
15). West Sussex: Wiley-Blackwell.
Schön, D. A. (1983). The Reflective Practitioner: How Professionals Think in Action. USA: Basic Books.
Sevaldson, B. (2004). Designing Time: A Laboratory for Time Based Design. In Future Ground (pp. 1–13).
Melbourne: Monash University. Retrieved from http://www.futureground.monash.edu.au/.
Sevaldson, B. (2005). Developing Digital Design Techniques: Investigations on Creative Design Computing (1st
ed.). Oslo: Oslo School of Architecture and Design.
Sevaldson, B. (2011). GIGA-mapping: Visualisation for complexity and systems thinking in design. Nordes ’11:
The 4th Nordic Design Research Conference, 137–156. Retrieved from
http://www.nordes.org/opj/index.php/n13/article/view/104/88
Sevaldson, B. (2012). Systems Oriented Design for the Built Environment. In M. Hensel (Ed.), Design
Innovation for the Built Environment - Research by Design and the Renovation of Practice (pp. 107–120).
Oxon: Routledge.
Sevaldson, B. (2013). Systems Oriented Design: The emergence and development of a designerly approach to
address complexity. In J. B. Reitan, P. Lloyd, E. Bohemia, L. M. Nielsen, I. Digranes, & E. Lutnaes (Eds.),
DRS // CUMULUS 2013 (pp. 14–17). Oslo: HIOA. https://doi.org/ISBN 978-82-93298-00-7
Sevaldson, B. (2015). Gigamaps: Their role as bridging artefacts and a new Sense Sharing Model. In Relating
Systems Thinking and Design 4 (pp. 1–11). Banff: Systemic Design Research Network. Retrieved from
https://app.box.com/s/tsj7ewtcy9dr63knf64tvo3yrepmzdov
Sevaldson, B. (2017a). Editorial. In B. Sevaldson (Ed.), Relating Systems Thinking and Design 6: Environment,
Economy, Democracy: Flourishing Together (p. 1). Oslo: Systemic Design Research Network. Retrieved
from https://systemic-design.net/rsd6/rsd6-proceedings/
Sevaldson, B. (2017b). Systems Oriented Design. in preparation.
Sevenhuijsen, S. (1998). Citizenship and the Ethics of Care: Feminist Considerations on Justice, Morality and
Politics (1st ed.). London: Routledge. https://doi.org/10.4324/9780203169384
Sidorová, M., Gaberle, M., Davidová, M., Hanzlík, K., Roubalová, L., Prokůpek, M., … Bakay, L. (2013). Ulice
- O strom více / Street -One More Tree. (M. Sidorová, M. Gaberle, M. Davidová, & K. Hanzlík, Eds.) (1st
ed.). Prague: reSITE. Retrieved from http://docplayer.cz/1288913-Ulice-o-strom-vice-praha-7.html
Thermos. (2006). Carduelis Chloris - Berry. Retrieved March 8, 2018, from
https://commons.wikimedia.org/wiki/File:CarduelisChlorisBerry-edit.jpg
Trepte, A. (2013). Phylloscopus Collybita. Retrieved March 8, 2018, from https://www.photo-natur.net/
United Nations. (2015). Transforming our World: The 2030 Agenda for Sustainable Development. General
www.FormAkademisk.org
29
Vol.11 Nr.4 2018, Art. 5, 1-30
Marie Davidová and Kateřina Zímová COLridor
Assembley 70 session (Vol. 16301). New York. https://doi.org/10.1007/s13398-014-0173-7.2
United Nations. (2016a). 11: Sustainable Cities and Communities - Sustainable Cities : Why They Matter.
Sustainable Development Goals. New York. Retrieved from
http://www.un.org/Sustainabledevelopment/Cities/
United Nations. (2016b). 15: Life on Land - Life on Land: Why It Matters. Sustainable Development Goals. New
York. Retrieved from http://www.un.org/sustainabledevelopment/wp-content/uploads/2016/08/15_Whyit-Matters_Goal15__Life-on-Land_3p.pdf
Vogel, G. (2017). Where have all the insects gone? Science, 5(6355), 1–4.
https://doi.org/10.1126/science.aal1160
Wong, E., Hogan, K., Rosenberg, J., & Denny, A. (2016). Reducing Urban Heat Islands: Compendium of
Strategies Urban Heat Island Basics. Washington. Retrieved from
https://www.epa.gov/sites/production/files/2014-06/documents/basicscompendium.pdf
Zieglerová, D. (2017). Monitoring výskytu netopýrů na lokalitě Zvonařka, Praha 2. / Bat Moniutoring at
Zvonařka Locality, Prague 2. Prague.
Zímová, K. (2016). Pilotní studie - Ekologický význam lokality Zvonařka, Praha 2 / Pilot Study - Ecological
Impact of Zvonařka Locality, Prague 2. Prague.
‘Biotope: A region that has a characteristic set of environmental conditions and consequently a particular type of fauna and
flora (biota)’. (Oxford University Press, 2004)
2
‘A point of particular significance is that local extinctions are common events (see Section 7.5), and thus the recolonization
of habitat fragments is critical for the survival of fragmented populations. Thus, particular attention should be paid to the
spatial relationships amongst fragments, including the provision of dispersal corridors. There are potential disadvantages. For
example, corridors could increase the correlation among fragments of catastrophic effects, such as the spread of fire or
disease, but the arguments in favour are persuasive’. (Begon, Harper, & Townsend, 2006)
5
‘Environment is the physical and biological surroundings of an organism. The environment covers non-living (abiotic)
factors, such as temperature, soil, atmosphere and radiation, and also living (biotic) organisms, such as plants,
microorganisms and animals’. (Oxford University Press, 2004)
6
The division between ‘participatory design’ and ‘co-design’ is used here in the meaning as discussed by Sanders and
Stappers (Sanders & Stappers, 2008) and it is commonly used in Central Europe in this sense. In this sense, participation
means that the related stakeholders are invited to the discussion board, while co-design means ‘co-creation’ (Sanders &
Stappers, 2008), where the stakeholders play a creative, active role within the design process as co-authors.
7
Ecosystem was described by Allen and Roberts as an ecological system inside the system that includes the geophysical part
(Allen & Roberts, 1993).
1
‘Sorption; is a word used in wood material science that refers to the absorption of any vapour or liquified
matter by a fibre.
9
‘For designers who are exploring new shapes using generative algorithms, Grasshopper® is a graphical
algorithm editor tightly integrated with Rhino’s 3-D modelling tools. Unlike RhinoScript, Grasshopper requires
no knowledge of programming or scripting, but still allows designers to build form generators from the simple to
the awe-inspiring’. (Davidson, 2017)
10
DIY means ‘do it yourself’.
11
Learning by doing refers to a theory of education expounded by American philosopher John Dewey. He
theorised that learning should be relevant and practical, not just passive and theoretical. He implemented this
concept by establishing the University of Chicago Laboratory School. (Pegg, 2018)
8
www.FormAkademisk.org
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