DIG STUDIO:\\
Indeterminate Landscapes Jordan Bell \\ Tera Hatfield \\ David Tomlinson
A thesis submitted in partial fulfillment of the requirements for the degree of
Masters of Landscape Architecture
University of washington 2012
committee:
Tha誰sa Way
Program Authorized to Offer Degree:
Landscape Architecture
INDETERMINATE LANDSCAPES
DIG STUDIO:\\
JORDAN BELL // TERA HATFIELD // DAVID TOMLINSON
This thesis is an interactive physical object. Due to the digital format requirement, this document is built from the constituent parts of the object. To view the original document, contact the department of Landscape Architecture.
PAMPHLET INDEX
APPENDIX A TANK FARM GAME 1
ALBINA RAILYARD
CONTAMINATION INDEX
PHYTO
GAME 3
LITERATURE
AXIOM REGIONAL ANALYSIS LABOR WHEEL
METHOD MCCORMICK & BAXTER GAME 4
LOCAL ANALYSIS
SCHNITZER STEEL GAME 2
SCRIPT SET
END SCRIPT
A PROPOSAL FOR AUTONOMOUS ECOLOGIES //EMBRACING ENTROPY
AXIOM
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DIG STUDIO is a collaborative, transdisciplinary design project focusing on the spatial inquiry of post-industrial landscapes that engage technical bioremediation tactics, experimental visualization methods
Groundwork Overview
and social outreach, particularly through installations and exhibits. A major component of the project examines the process of investigation, experimentation and intervention, and how that is translated to the general public through the landscape, art and information design.
//UNDER THE PAVING-STONES, IT’S THE BEACH! —Situationist inscriptions on the walls of the Sorbonne, May 1968 Student Revolt
DIG STUDIO began by describing a distinct vocabulary as a means to discuss our project linguistically, ecologically and spatially. In its initial conversations, DIG STUDIO sifted through adjacent terms (to postindustrial) that referenced irregular and uncertain conditions within the contemporary landscape. The multiplicity of applicable terms identified suggested that conditions in certain landscapes can be in flux, and illdefined in scope, depth and perception. These fluctuating conditions originate in the recent emergence of a new disturbance regime. The term industrially-modified site is employed to characterize those {sites} in which the disturbance may be traced back to an industrial process bracketed in time by the rise of modern chemical engineering and refineries.
Categorically, industrially-modified sites generate
many instances of “other” as conventional conceptual systems erode.
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Traditional ecological disturbances have now been coupled with industrial disturbances, producing new ecologies, indeterminate boundaries and unreferenced geographies. We propose to investigate these geographies through spatial analysis, the development of appropriate modes of representation, and the study of techniques with which to reclaim them— linguistically, ecologically, and spatially. DIG STUDIO seeks to establish operational matrices and develop tactical deployments that re[in]habit and reclaim sites and landscapes that have been modified, degraded or disturbed by former industrial trajectories and that suffer from ecological amnesia. DIG STUDIO is Leann Andrews, Jordan Bell, Tera Hatfield, David Tomlinson.
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Disturbed sites are “spaces where matter, flow, and wastes know no boundaries” (Meyer 65). Disturbance is a category of critical ecological processes that generate patchwork landscapes of differing scales, resulting in complex ecosystems. Periodic occurrences of
Strata: introduction of topos Archeology & entropic natures
these
disturbance-events constitute a disturbance regime. Within a given disturbance regime, an ecosystem may vacillate between various habitat types with a more or less predictable successional set of species, where the dissipated energy from previous sets is reclaimed in the next. A regime shift occurs when the disturbance is significant enough to affect the entire cycle of successional regeneration, such as a volcanic eruption,
//NEITHER LANGUAGE NOR LANDSCAPE IS NEUTRAL OR STATIC...WE UNEARTH SHIFTING IDEOLOGIES AND UNLEASHED TOXIC SUBSTANCES. —DIG Studio
the practice of fire suppression, or climate change. However, within these historical disturbance regimes a new regime has been emerging across innumerable territories. Instigated by industrial activities, this shift not only alters entire ecosystems, but our entire understanding of them as well. Species never recorded before, such as within Butte, Montana’s Berkely Pit, have been found living on-site in anaerobic conditions immersed in toxic sludge and metabolizing with elements never thought to be viable for life (Gugliotta WIRED 5.09). Thus, the very definition of disturbed sites is often in flux—much like the landscape, it momentarily shifts and swells, collapsing while at once rebuilding through a series of thermodynamic processes.
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Just as this emerging regime shift produces new ecologies, it forces us to
Once abandoned, the maintenance of those boundaries is unhinged—the
accept new ideas of landscape as well. These sites are not separate from
effects of time and the forces of entropy are left to create outputs that
“our places of home, regardless of physical distance. Toxicity flows. It
are not easily translated, incorporated, or otherwise integral to a pre-
transgresses property lines, watersheds, even ecosystems” (Meyer 65).
existing fabric— conceptual, social or otherwise.
As a result, there is a collapse in meaning between site and non-site, resulting in a confusion that originates from the transgression and break
DIG STUDIO’s design foundation relies upon the supposition that the
down of traditional boundaries, producing an ambiguity between that
theory of entropy applies to language as well as the landscape, and in
which is nature/natural and that, which is manipulated/constructed. This
particular to industrially-modified sites. Neither language nor landscape
“confusion” also stems from our socialized reliance on political territories
is neutral or static, but rather a carrier of fluid, disjunctive, cultural and
and culturally reinforced jurisdictions which do not correspond to these
social values. Within the archeological and ecological strata we unearth
flows, but which are arbitrarily imposed upon the natural terrain (however
shifting ideologies and unleashed toxic substances.
familiar they may have become). Our own waste streams sabotage our codified landscapes, territories, and notions of “time,” “place” and “here”. Toxicity flows in and out of site and sight, above and below. Here, entropy occurs not only in thermodynamic processes, but in conceptual and representational systems as well. DIG STUDIO seeks to expose entropy through the attenuation of maintenance regimes, investigating opportunities for subtly “managed” systems. Boundary conditions at active industrial sites are the work of constructed human maintenance regimes (whether successful or not).
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DIG STUDIO proposes to investigate and translate expanded definitions (read: boundaries) of toxicity and infrastructure (and therefore industrially modified sites) in order to explore and re-characterize these sites/counter
Value of risk & uncertainty
Translation & transgression of strata
sites, reoriented towards the urban context, the human body and fluctuating timescapes. Transgression and transformation play an essential role in exploration and engagement of disturbed landscapes because they are [dis] placed in their conceptualization [abjection] and physical manifestations, often cordoned off—with fencing, remoteness, or both. DIG STUDIO will study the inclination to transgress and translate boundaries found in culture,
//THE DREAM OF ARCHITECTURE IS TO ESCAPE ENTROPY. —Robert Smithson
nature and cities that characterized the work of theorist Henri Lefebvre and the Situationists. In response, DIG STUDIO will test, tackle, transform and translate the very act of experimentation and risk—to investigate while intervening. During this process, DIG STUDIO will ask what contextually appropriate tactics might be used to visually or physically engage and re[in]habit these spaces. How can we embrace these evolving changes and opportunities for transformation? DIG STUDIO proposes to answer these questions with a design and research based project, examining the ever changing Willamette industrial basin of Portland, Oregon through the lens of selected disturbed sites and frames.
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DIG Studio
Jordan Bell Jordan is a graduate student in Landscape Architecture at the University of Washington. He has a background in sculptural pursuits as well as
Biographies
various fabrication techniques and materials. He is interested in sculptural representations of space. He has worked in various positions in landscape architecture firms and as a surveyor prior to starting graduate school. Jordan holds a BFA with concentrations in metal fabrication, casting and ceramics as well as a BA in Environmental Studies focusing on human relations to the landscape.
Tera Hatfield Tera is a graduate student of Landscape Architecture and Urban Design at the University of Washington. She is a 2012 National Olmsted Scholar Finalist as well as the recipient of the Finrow Endowed Rome Fellowship and the Copeland Endowed Fellowship in Urban Design to study infrastructure anchored to the Tiber River. She is interested in collaborative work on post-industrial landscapes and urban green infrastructure that engages experimental research and representational methods while serving as public educational outreach. Prior to attending design school, she was a writer and graphic designer in New York City. She received her B.A in English from Vassar College.
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David Tomlinson David is a graduate student in Landscape Architecture at the University of
graveyard of the Rustbelt including urban vacant lots, brownfields,
Washington. He recently received the Valle Scholarship and International
interchanges, abandoned factory buildings, and industrial campuses.
Exchange Fellowship and is currently an independent researcher at the
Leann is interested in investigating ecology and landscapes as a tool
Stockholm Resilience Center, Sweden, where he is investigating resilient
to increase holistic health (environmental, social, economic, ecological,
ecological infrastructure and its relation to existing and emerging
physical, mental health etc.) at the personal, community and global
social-ecological networks. He is also collaborating on several projects
scales. Her undergraduate studies were in Landscape Architecture and
including the refinement of a proposal for a new Stockholm University
Dance at The Ohio State University.
campus in the National Urban Park, a project which blends Landscape Urbanism principles with resilience theory. Prior to enrolling at UW, he was a practicing architect, designer and luthier, living in the San Juan Islands where he also spent many seasons as a kayak guide. He earned his Bachelor of Architecture from the Cooper Union in 2002.
Leann Andrews Leann is a graduate student in Landscape Architecture and Global Health at the University of Washington where she manages the Green Futures Lab, an interdisciplinary research, design and education lab.
Leann
leads a duel life as a licensed landscape architect and performing artist, with professional backgrounds in Green Infrastructure design and postmodern dance. She has designed a variety of sites in the industrial
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Committee
Thaisa Way (chair) Associate Professor, UW//LA-ARCH
Advisory team
Thaisa Way is a landscape historian teaching history, theory, and design. Dr. Way’s research considers how diverse approaches have shaped and informed relationships between people and landscape, cultures and nature, and practices and profession.
Ken Yocom (advisor) Assistant Professor, UW//LA-ARCH Ken‘s professional and academic interests explores the intersections between the ecological sciences and the design and management of landscapes. In particular, Ken is interested in the relationships and ecologies of natural and socio-economic processes that form and sustain the patterns of our urban environments. He views the activities of the allied design professions as catalysts for identifying, understanding, designing, and managing the inherent potential found within our built environments.
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Grounding Design
LITERATURE
01
0.1 Intro Framed
by
contemporary
knowledge ecology,
and
research
landscape
in
urbanism,
and industrial ecology, DIG STUDIO engaged in a complex interweaving of design process and
intellectual
investigations
into
post-
industrial reclamation. The body of knowledge reviewed below represents the initial, pre-design investigation into the existing literature. Topics from ecology, landscape urbanism, landscape ecology, resilience theory, sociology, architecture, art and industrial history were examined as a means of grounding the subsequent design process. This review serves as an anticipatory act to the design process—one that seeks to delineate a territory of relevance, influence, and compatible thought. It is by no means exclusive nor exhaustive. Rather, it is intended to establish theoretical parameters as well as an initial vector of approach to an as-yet unidentified site, and
an as-yet indeterminate design process. Three
around the sun, and opened the heretic’s door to
writes
Likewise, in Ecology and Design (2002), Karr
primary areas of concentration were established
the recognition of the solar system. In short time,
…we generally understand the effects that urban
(2002) reports Ehrlich’s 1997 observation that
by DIG STUDIO early on in the process: urban
this duly lead to the development of cosmology,
development may have on ecological processes,…
“Ecology is ‘packed with papers describing more
ecology;
post-industrial
resulting in an indeterminately signified condition:
[but d]oes an increase in urban development have
and more sophisticated analyses applied to more
reclamation. These themes inform the structure
our location in the Universe as just an average
a linear effect on ecological processes? Or can
and more trivial problems,’” (p111).
and content of the review below.
planet in an average solar system in an average
we detect thresholds, and/or differentiate among
Alberti’s investigation is not trivial, but how and
galaxy (Gribbin 1999), one without absolute
types of development patterns?”(p17)
where can it, and should it, be applied?
significance.
One is left to wonder what significance this
goes on to cite Pienkowski & Watkinson (1996)
research may have beyond its pure modeling
analysis “of 60 papers published over thirty years
1.1
indeterminacy;
and
Ecology & Design
Clearly, Karr
Ecological systems have always been complex. It
This indeterminate condition parallels Huserll’s
efficacy, or if such research is merely relegated
in the Journal of Applied Ecology…[showing] that
is only recently that the tools have been developed
“crisis,” in which modern science has “’reduced
to the mathematical instrumentality of predictive
most articles lacked practical applications or
to understand them as such. It is, in many ways, a
nature to a mathematical manifold’,” (Corner,
modeling.
management recommendations,” (Karr 2002,
continuation of the epistemological mechanisms
1990) resulting in what Corner (1991) regards as
mathematical
urban
p137). The implication is that either scientists
of the Copernican revolution, where techne,
“modern techno-scientific thinking, perpetuating
development and ecological processes at one
are too consumed by solving mathematical
uncoupled from poesis, (Corner 1990) provided
an excessively ‘hard’ world in which culture
point in time be useful—or even relevant—
complexities within their isolated systems of
the basis for revelatory insight.
The question,
cannot simply figure or recollect itself,” having
in determining it at another?
And assuming
variables, or that practical applications are not
however, is not purely one of instrumentality
been deprived of both its symbolic center and its
individual variables can be dis-aggregated, would
feasible within the current modes of investigation.
(ibid), but of significance versus the signified.
mimetics. Hardness here may be refined to mean
not one variable—like the value of currency, or
Re-conceptualizing the “universe” as heliocentric
without a cosmic center, and therefore perpetually
land— affect the entire predictive capacity of the
These remarks are made within the larger
undermined the Cathollic Church’s theological
analytical. This condition is clearly evident when
model?
context of the growing dichotomy between two
position, inspired the organization of Versailles
the ecological urbanist Marina Alberti (2008)
02
Will
knowing
the
relationship
approximate
between
applications of ecology: as a research science and
03
Literature
Grounding Design
as a component of a management strategy. Karr
the shear complexity of the method of scientific
applications of ecological research remain to be
well to conservation efforts which select a species
of systems if those theories are also based on
their diachronic nature.
(2002) suggests that our knowledge of the current
research sidetracked science from the original
documented or implemented.
as a mascot for consensus building. These efforts
other systems, be they social or political.
successional diagrams in Downsview Park & Fresh
problems that constitute “biotic impoverishment”
intention of the research.
stem in part from a division in ecology between
view parallels Corner’s earlier description of the
Due in part to the overwhelming complexity
ecological. However, conservation efforts are not
The integration of ecological knowledge into the
in Olmsted’s management plans for certain
scientists
uncoupling of techne from poesis (Corner 1990),
of total-systems understanding, especially in
the only socially oriented aspect in ecology. In
design process, then, must account for several
parks, wherein he specified the gradual selective
Ecologists typically study particular phenomenon,
discussed above.
But from Karr’s perspective,
regards to ecological systems, concepts such
fact, ecology may be as much a social construct
discrepancies.
These include the differences
thinning of tree stands, rather than a formal
while natural resource managers typically study
science is endlessly circling an unacknowledged
as indicator species, processes and events have
as it is a scientifically verifiable one.
between the unknown affects on an entire
planting arrangement, thus presenting a to-be-
how to maximize particular yields, ignoring much
center, while for Corner, science seems to have
been put forward as a means of interpreting un-
system versus the measureable affects on a
determined stand of trees, and forgoing formal
of everything else. Karr (2002) continues tracing
followed its natural trajectory. It’s worth noting
quantified changes in
Poole et al (2002) acknowledge the socially-
proxy keystone species. These also include what
planting schemes. The growth and succession of
this dichotomy back to a schism in scientific
that within Karr’s critique of scientific research
serve as proxies to larger systemic relationships
constructed aspects of ecology.
For example,
processes and affects are emphasized or de-
plants, either by natural or anthropogenic means,
ideas two-hundred years ago through A. Sach’s
divergence, Karr does acknowledge one category
and contribute to the articulation of a set of
theoretical frameworks, or what constitutes an
emphasized. Thirdly, the social-political context
provides one indication of temporality.
(1995) summary of von Humboldt’s quest to
of application-based ecology: the delivery of
potential metrics.
These proxies are often
actual benefit, are parameters that are chosen.
in which ecological knowledge is generated within,
develop a ‘unifying theory’ of natural phenomena,
recommendations regarding wildlife management.
termed key species, key processes, and key
Poole et al also note how these choices may differ
or applied onto, will influence its integration into
Another essential component of this investigation
the emergence of science, and the subsequent
This overlap and potential integration is evidenced
events (Johnson et al 2002b). Examples of some
between different groups. Take, for example, the
a design. It may be that what has been chosen to
is the abiotic processes, such as erosion and
specialization of science. This specialization (for
in aspects of the Seattle Waterfront development
key species are well known, such as the salmon
discrepancy between research ecologists and
be measured is in fact not a predictor of overall
sedimentation, that play a critical function in
Karr and for Sachs) clouded society’s view: the
planning in the approach to juvenile salmon, for
in Washington State, or the wolf in Montana. In
natural resource managers discussed above. At
systems behavior, but a socially selected variable.
landscape formation and design.
ideas and components of systems became more
example. Other examples include more regional
each case, the absence of the species results in
the same time, Karr (2002) points to Schneider’s
significant than the system itself. As scientific
work employing graph theory to map potential
noticeable and system-wide alterations to the
(1997) emphasis on addressing interdisciplinary
Despite these uncertainties, there are process-
park as an example, in which sediment transport
research departed from van Humboldt’s original
corridors, and wildlife crossings at freeways,
ecosystem in which it resides. For this reason
integration
based elements that are integral to many
was physically modeled and the resulting fluvial
quest—to identify humanity’s position within
as in Jones & Jones design/ planning project
they are also termed “keystone species” (Paine
complicated social-political contexts.
landscapes.
geometries
the larger context of interconnected systems—
located along I-90 in Washington. Other direct
1969). Certain keystone species lend themselves
ecology is even more complex than just its theory
and
natural
resource
managers.
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Karr’s
point
of
are as much social undertakings as they are
larger systems.
These
of
ecological
knowledge
within Surely,
This is evidenced in
Kills proposals, among others. It was also present
Czerniak
(2002) describes Hargreave’s Guadalupe River
These elements are manifested
through their change over time, that is, by
05
manifested.
These
geometries
present both a representation of a process as
well a simultaneous embodiment of it. This two-
degrading them. In some cases, these processes
to an irreconcilable condition within landscape
and was used to compare possible consequences
fold presentation is quite different from Eisenman
are easier to model and understand than larger,
architecture: the imperative to work with natural
stemming from different priorities. It is of interest
As with multiple spatial-scales, multiple time-
patterns may never be fully understood. Long-
& Olin’s Rebstock Park1, in which ground is
more complex and potentially indeterminate
processes in order to benefit the well being of
that the most certain outcome (for all 3 scenarios)
scales are necessary and crucial components of
phased feed-back loops may not even be readily
considered and manipulated (Czerniak 2002),
ecological processes.
ecological and social systems, and the inability to
was the increase in fresh water consumption.
understanding feedback loops. The ecologist S.
apparent yet, and, as in Carpenter’s (2001)
Carpenter (2001) breaks down feedback loops,
example of Lake Mendota, WI, alterations to some
but process is relegated to intellectual privity,
truly understand the larger systemic permeations
(ibid). The impacts of contemporary urbanization
“’…which becomes a topologic event /structure,’
The question, then, for landscape architecture,
of such work. The process of verification is not
It would be a mistake to restrict consideration of
or adaptive cycles, into four stages: (i) rapid
natural processes may be irreversible due to a
that
subsequently
is how can indeterminate ecological systems
only elongated with respect to other design
ecological processes to regional scales. Certainly
growth-r; (ii) conservation-K; (iii) collapse-Ω; and
new state of resilience (see section 1.4).
reframes—normative relationships…” (Czerniak
knowledge be incorporated functionally, and
disciplines, such as architecture, it may also be
the smaller scale of site embodies the same
(iv) renewal and reorganization- α. Alberti (2004)
2002,
George
simultaneously, within a landscape that embodies
asymptotic—having no clear means of verification.
principles. And S. Steingraber’s (2002) poignant
notes that “feedback is phased-lagged often
Hargreave’s Guadalupe River project, Kristina
and figures meaning? In other words, how can
essay takes this down to the level of the body as
by decades,” and that the cause and effect are
Hill (2002) exhibits her interventions in the Shop
potentially conflicting interpretations of place
at some length. She says that not only is “[u]
well, all the way to amniotic fluids.
typically not correlated nor clearly connected.
Creek Wetlands—sand and concrete berms that
and science coexist within a ‘singular’ design with
ncertainty … intrinsic to ecology,” but that “[t]
changes happen slowly, often at the scale of
slowly erode over the course of time while slowing
geographic specificity?
here is rarely a clear link between one cause
site, (Hill 2002) before it is documented at the
In the case of urban landscapes, feed-back loops
degree of urbanization, as well as changes
and a particular effect,” (p423). Her proposed
regional scale, and it is perhaps more feasible to
may not only be phase-lagged, but geographically
within the epistemology that has developed
solution is to explore “probable outcomes” and
notice such changes at this smaller scale These
displaced as well.
around it, have introduced new ways of thinking
“multiple
iterations…”
small changes in system patterns at one scale
magnitude of the disturbances.
Through the
about urbanization, landscape, and ecology.
(p423). A similar strategy was implemented in
can generate instability at another scale (Alberti
processes of urbanization, natural landscapes
Alberti (2004) argues that “urban ecosystems
are
are
have a chance to change trajectory toward
inevitably p114).
dissolves—yet With
similarities
to
flood waters to allow for both sedimentation and a decrease in the rate of erosion upriver of the reservoir. Stormwater runoff is yet another process shaping innumerable projects.
1.2 Ecology, Design, & Indeterminacy
The
Kathleen Poole et al (2002) discuss this
expressions,
various
Ecological
1.3 Design & Urban Ecology Urbanization, as well as the study of it (urban ecology) both unfold slowly through time.
This is due in part to the
The
management of abiotic processes may, in turn,
Given the discussion above, it is not likely that
a stakeholder workshop entitled “Conservation
2004).
affect
landscape architects should be expected to
2050,” (Baker 2004). This workshop was based in
scales may lead to statistical relationships but
introduced, manufactured landforms and patches
the development of self-organizing processes
predict the exact ecological outcomes of their
modeling the probable outcomes of stakeholders’
may overlook important feedback loops (Picket &
are produced, and biological heterogeneity is
of interacting ecological and socio-economic
works.
visions for the future of the Willamette River Basin,
Ostfeld 1994).
minimized through homogenous land-use patterns
functions,” (p249). Others have shown that this
1
ecological
processes—enhancing
or
See Fischer, Volker, Frankfurt Rebstockpark: Folding
in Time. © 1992, Prestel.
However, these outcomes contribute
06
Also, examining relationships at larger
modified,
bio-geographic
07
barriers
state would indeed be a new state of resilience,
anticipates one method of investigation for urban
in Linda Pollak’s (2007) contribution to Large
small scales operating simultaneously in a site,
and offers an acknowledgement within the
able to provide a structure from which to explore
and be bounded by a new set of attractor domains
ecological reclamation, the restoration of essential
Parks (2007), entitled ‘Matrix Landscapes. In
to allow the making and interweaving of radically
operational and generative process of design
multiple outcomes to design and management
(e.g. Carpenter 2001, Holling 2001, Sheffer 2001,
ecosystem services, and a trajectory for future
‘Matrix Landscapes,’ Pollak (2007) proposes a
different kinds of places…(pp102-103)
that plurality, multiplicity, and indeterminacy are
decisions.
Picket & Ostfeld 1994).
Given an ecological
urban design. Some new developments include
new strategy for dealing with complex processes
Pollak traces each entry’s submissions in terms
deeply and intricately woven within such complex
system with the potential for multiple-branching
green roofs (e.g. (Oberndorfer 2007, Baumann
over time, and one which attempts to incorporate
of their matrix. Mathru/da Cunha + Tom Leader
sites. Pollak wisely includes Corner’s statement
into various states after a loss of initial resilience,
2006, Brenneisen 2006, Kohler 2006), and
indeterminacy alongside long-phase processes.
Studio use surface, field, datum, edge, and
that the proposal “is as much about the ‘design
Sheffer (2001) states:
vegetated walls systems (e.g. Tomlinson 2011).
Pollak notes that “three out of six proposals for
zone, aligning them with five different materials
of a method of process of transformation as it
…to induce a switch back to the upper branch,
However, these developments do not necessarily
the Fresh Kills competition utilize some kind of
present at Fresh Kills. In Hargreaves proposal,
is about the design of specific places,’” (Pollak
it is not sufficient to restore the environmental
consider
mathematical matrix to represent the project,”
matrix is understood to refer to a “’mold in which
2007, p113).
conditions of before the collapse (F2). Instead,
scales, or time frames in their design, but rather
(ibid, p103).
She attributes this development
a thing is cast or shaped,” (Pollak 2007, p105).
one needs to go back further, beyond the other
comprise instances within larger (voluntary)
to the need to organize “multiple forms of
In this proposal, transformation, succession and
Matrices are one strategy that may be adapted to
define an ecosystem as: ‘‘a set of interacting
switch point (F1), where the system recovers by
planning strategies.
Likewise, many of these
documentation [that] interact dynamically,” (p99)
operation each linked to a different temporal
begin to deal with the representation of dynamic,
species and their local, non-biological environment
shifting back to the upper branch. This pattern,
strategies address a limited scope of processes
and “multiple parameters,” (p100). She proposes
structure, and comprising three environments:
interacting site processes.
functioning
in which the forward and backward switches
over time.
that a design matrix can:
Domain, Meadows, and Lake Island.
useful in developing strategies for ecological
Moll and Petit 1994).
… support the construction of a kind of unity that
Operations’ proposal is comprised of three
restoration,
and
processes provide ecosystem services that are
aggregated
ecological
processes,
occur at different critical conditions, is known as
Field
1.4 Ecological Grounding: Landscape Ecology, Adaptive Cycles, and Resilience. The ecologists Bolund and Hunhammar (1999)
urban-ecological
Matrices may be interfaces,
together
to
sustain
life,”
(after
Aggregated ecosystem
hysteresis (p591).
For complex sites, re-deployment of instance-
does not rely on a single vision or overarching
element sets (three matrices): threads, islands,
bioremediation of legacy contaminants.
The
defined as: ‘‘the benefits human populations
While the above hypothetical case of hysteresis
based strategies such as green roofs will not
order to manage in creative and operation terms
and mats, operating “as a strategy, a figure, and
matrix organizes, but leaves the designer free to
derive, directly or indirectly, from ecosystem
corresponds
natural
necessarily be entirely effective, and certainly
the interactions between multiple perspectives,
a device of representation,” (ibid, p107).
This
proceed from there. The matrix also allows for
functions.’’ (Costanza et al 1997). The practice
significance
are not responsive to complex site processes
scales, and types that attend the development
multiplicity of matricies avoids the abhorred
the recognition of the semantic variability within
of urban ecology, (e.g. Berry & Kasarda 1977,
A lb e r t i’s
and context. An alternative strategy for dealing
of a complex urban ecological landscape…
“slavery to oneness” (Hargreaves 2007, p171)
ecology—of terms such as resilience, adaptive
Picket et al 2008) or the study of the interface
statement of self-organizing ecological processes
with complex sites and landscapes is suggested
acknowledge the relationships between large and
even within the operation of the matrix itself,
capacity, and ecosystem services.
of ecological systems—both naturally occurring
ecosystem,
to it
disturbance
may
have
of
great
for urban ecosystems as well.
a
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09
It may be
and anthropogenic—seek to modify current
regimes.” That is, a given landscape has a
five types of landscape patches that contribute
Mosaics, 1995.
urban design practices in order to provide a
discernible structure consisting of relatively
to the generation of the landscape mosaic within
provides a structural, relational and situational
Beyond spatial patterns, the notion of specificity
historical and contemporary fisheries in the Great
more resilient network of ecosystem services
homogenous units, often referred to by ecologists
an overall landscape matrix: spot disturbance
system
analyze
carries with it an unknowable quantity and
Lakes, perch populations in Lake Windermere,
(e.g. Alberti 2008).
The analysis of complex,
as stands, which in turn have similar “frequencies,
patch; remnant patch; environmental resource
heterogeneous landscapes.
His research has
quality of information. Recent work in systems
and vegetation structure in grassland grazing
urban and natural landscapes, their interactions
intensities, and types of individual disturbances”
patch; introduced patch; and ephemeral patch.
provided the foundation for landscape planning
theory and research in ecology has led to the
areas of the American West. The domain shift in
and interdependence is rooted in several related
(p733). This works at multiple scales and Forman
Examples of each vary within the subsequent
across multiple disciplines and jurisdictions
development of resilience thinking. Resilience is
grazed grasslands, in which cessation of grazing,
concepts, namely landscape ecology, adaptive
(1981) acknowledges that ecological principles
literature; however, their ultimate theoretical
nationwide
as
a multifaceted term that may be defined briefly as
after a certain point, does not result in the return
capacity, and resilience thinking. Each of these is
can be so applied, however, their applications are
classification may not be absolutely critical to the
mentioned, launched an entirely new discipline.
the ability of a system to experience intermittent
of grasslands, was observed on Stora Karlso, an
discussed below as they were primary conceptual
customarily limited in scope for pragmatically
overall landscape mosaic.
It has informed—directly or indirectly—countless
disturbance.
The measurement of resilience,
island in Sweden grazed by sheep, as well. Holling
components within DIG STUDIO.
experimental reasons.
projects since its publication.
and therefore the specificity of a certain system,
uses these cases to identify distinct domains
located geographically and ecologically, is a
of attraction in closed ecological systems.
The delineation of a
with
Forman’s
which
and
to
study
research and
internationally,
and,
as “domains” (p10).
These examples include
landscape, or of an ecosystem for that matter, is
Forman (1981) goes on to identify patch size,
Richard Forman largely pioneered the field of
variable, and depends upon both the goals of the
edge, shape, quantity and configuration as
An objective of studying landscape mosaics is to
current topic at the forefront of science. What
qualifying their states as “domains,” (ibid),
landscape ecology.
researcher and the spatial limits of the study. If
additional significant characteristics of patches
illuminate the underlying ecological and abiotic
follows is a history of the term resilience and a
Holling is careful to state that these theoretically
the
one is examining the relationships among micro-
that contribute to the landscape mosaic.
(geomorphic,
and
discussion of its usage in the scientific literature,
determinable models differ from actual systems,
larger landscape context in which ecological
invertebrates, the ‘ecosystem’ in which these
this set, he proposes two more features of the
promethean) processes behind their generation.
in an effort to better qualify the application of the
where indeterminacy is more prevalent, and a
disturbances and processes could be identified
are considered may be restricted to the riparian
landscape mosaic: corridors and habitations.
It is the processes that generate the mosaic, and
term within the DIG STUDIO design phase.
comprehensive analysis is often limited by data
and understood. Drawing on this work, Forman
substrate in which they live. However, this does
Corridors provide connectivity between patches.
the mosaic that signifies a certain specificity,
(1981) suggests that a “landscape’ is a distinct,
not necessarily exclude the influence of “outside”
And habitation—significantly—refers to human
a particular place.
However, specificity is
The ecologist and resilience-thinking pioneer
measurable unit with several interesting ecological
forces.
dwellings and development. He elaborates upon
subject to modification, sometimes extreme
C.S. Holling (1973) enumerates several examples
Holling (1973) goes on to identify several other
these structural principles in his 1986 book
modification, depending on land-use pressures
of major changes in landscape specificity.
He
systems, including the Spruce Budworm outbreaks
Landscape Ecology, and further in Landscape
and management strategies.
refers to the differing states of such landscapes
in Eastern Canada. In this example, the longevity
mosaics,
and
By introducing patches,
corridors,
he
described
characteristics,” comprised of “recognizable and repeated clusters of ecosystems and disturbance
In this same research, Forman (1981) identifies
10
To
atmospheric,
hydrological
By
availability.
11
ecological system organizes itself in response to
resilience, is, ultimately, a “boundary object,” a
Resilience remains in these contexts a relative
specie’s population is often indicative of the
management actions (p438).
metaphor, like sustainability or biodiversity, that
term, dependent upon desired states, time, and
overall health of the ecological system in which
allows for cross-disciplinary cooperation—i.e.
space. Measuring resilience thus reveals its own
it resides.
While Folke focuses on the operational potential
ecological, societal, and economical.
However,
challenges. Carpenter (2001) points out that a
term resilience has taken on an adaptive life of
of the term resilience in social-ecological-systems
metaphor and science do not readily coincide.
turbid body of water can be resilient to restoration
Carpenter
during outbreaks, which are in turn dependent
its own, coming to signify different conditions
(SES), Carpenter et al (2001) also states:
Therefore, the authors argue that in science, this
attempts to re-establish a clear water state,
issueswith other terms such as adaptive capacity.
upon rarely occurring dry weather conditions.
in different circumstances (Brand & Jax 2007,
Resilience has multiple levels of meaning: as a
malleability of the term undermines the capacity
citing Lake Mendota, WI, as one example.
Accordingly,
Holling summarizes that concentrating on the
Carpenter 2001, Gunderson 2000). Necessarily,
metaphor related to sustainability, as a property
of experiments and studies to measure resilience,
terms of time, certain technologies may increase
capacity is the learning trend of a system (typically
“boundaries to the domain of attraction rather
the
systems
of dynamic models, and as a measurable quantity
e.g. Carpenter et al (2001):
a population’s resilience, as in the case of the
involving governance or management) to adapt
than on equilibrium states” allows one to identify
thinking that brought about urban ecology has
that can be assessed in field studies of SES
Although the metaphorical concept of resilience
iron axe and forest clearing to produce food, but
its practices in relationship to disturbances
two types of system behavior:
led to an evolution of the term resilience. Folke
(p765).
has the power to inspire useful analyses of
result over the longer term in a decrease in overall
(Carpenter et al 2001).
One can be termed stability, which represents
et al (2002) paraphrases previous publications of
In lieu of a definitive, categorical and scientific
socioecological systems, much more insight could
system resilience after a certain point of clearing
also been referred to as the capacity of an
the ability of a system to return to an equilibrium
the term:
understanding of the term resilience, Brand & Jax
be gained from empirical analyses, which would
is achieved (Ruthenberg 1976).
Likewise, the
ecosystem to attain multiple (non-synchronous)
state after a temporary disturbance; the more
Resilience,
is
(2007) propose a typology for the term resilience,
require an operational, measurable concept of
measurement of resilience is often dependent
states of equilibrium (Gunderson 2000). These
rapidly it returns and the less it fluctuates, the
related to (i) the magnitude of shock that the
citing 35 years of publications, including those
resilience (p767).
upon a “surrogate,” (Carpenter 2001), in which a
two definitions reflect the construct of a SESs.
more stable it would be. But there is another
system can absorb and remain within a given
previously cited, beginning with Holling’s 1973
The authors conclude, in a similar vein to
major biotic or abiotic process or characteristic
This transmogrification of a particular signified
property, termed resilience, that is a measure of
state; (ii) the degree to which the system is
paper.
The three main categories, descriptive,
Carpenter et al (2001) that the scientific definition
is adopted as an indicator, as in the case of
condition of one term to another signified
the persistence of systems and of their ability to
capable of self-organization; and (iii) the degree to
hybrid, and normative each contain sub-categories
or descriptive signification of the term must
phosphorus, livestock densities, or land use, in
condition (descriptive to hybrid, or hybrid to
absorb change and disturbance and still maintain
which the system can build capacity for learning
corresponding to separate applications of the
be refined and limited, without the normative
fresh lake systems (ibid). This parallels the usage
normative) suggests an evolving dialogue that is
the same relationships between populations or
and adaptation. Management can destroy or
term. Brand & Jax (2007) go on to enumerate
and hybrid signification being lost to the larger
of indicator species in ecology, such as salmon or
engaging a plurality of perspectives and spanning
state variables (p14).
build resilience, depending on how the social-
and explicate these categories, concluding that
dialogue.
orca whales. The overall health of the indicator
a wide variety of traditional disciplines.
of the budworm is dependent upon the length
These preliminary hypotheses, originally
of the re-growth cycle of spruce trees between
based on theoretical models, were tested in
outbreaks. The development of spruce ensures
various other systems by Holling’s contemporaries
food for future generations of budworms, whose
(Holling 2006). Over the ensuing decades, the
reproductive capacity is exponentially increased
emergence
for
of
interconnected
social-ecological
12
systems,
13
In
et
al one
(2001)
illuminate
interpretation
of
similar adaptive
Adaptive capacity has
place
(Norgaard
2009).
Unlike
resilience
revisions.
of the retinal image, allowing the subject to see
2.0 Site
Site, Scale, and the Somatic
the world as right-side-up once again.
One of the broadest conceptions of site
In A New Angel/Angle in Architectural Research
characterized as a conceptually problematic
can be found in Heidegger’s writings, in Building,
(Frascari 1990), the architect Michael Frascari
anthropogenic, have indeterminate outcomes.
one. On the one hand, site carries with it certain
Dwelling, Thinking.
describes methods of construction that align site-
This is attributed largely to their complexity,
traditional biases such as limits, implies a
describes the horizon not as a line, but as a
lines with celestial choreographies.
in time and space (e.g. long-phase feedback
certain scope of project based on square area or
mutable, expandable space, the site of dwelling,
stance is rooted in the Neapolitan philosopher Giambattista Vico’s assertion that while intelligible
Likewise, ecosystem services is a critical term
that began as a descriptor of an ecological
with multiple interpretations that informed the
process and subsequently was transferred to
Resilience thinking, as well as landscape ecology
DIG STUDIO project. The concept of ecosystem
other metaphorical significations, ecosystem
and systems theory, emphasize that outcomes
services was developed as a metaphor in order
services began as a metaphor and later was
of ecological processes, whether natural or
to make a stronger argument for conservation of
operationalized.
natural resources (Norgaard 2009). By pointing
2.1
The
notion
of
site
has
often
been
Here, Heidegger (1971)
Frascari’s
out that such services were limited, the argument
This
followed that they must be conserved.
institutionalization is important as a means
loops).
However, the terms used to delineate
geography, and typically conforms to arbitrarily
the site of mind.
Norgaard (2009) provides a brief history of
to understanding the essential framing of the
the parameters within which these outcomes
determined parameters such as plat maps and
offers an exquisite explanation of site.
In his
universals do exist, they are not likely to be
this argument, focusing on the shortcomings of
cultural readings of urban ecology as a practice
may be categorized as indeterminate are also
operative concepts of property.
On the other
experiments with special spectacles, in which
Cartesian in nature. Rather, they are derivatives
socially-derived terminology, and the conceptual
and as a critical stance. Janssen (2002), a spatial
variable
ecosystem,
hand, site conjures images of Cartesian specificity,
concave lenses are mounted to spectacle frames
of the embodied experience. Akin to Ponty’s
limits that become reified by such terminology.
economist suggests it is in the realm of social
ecosystem
indeterminacy
finiteness, manageability, and a discourse of
worn by a subject, he demonstrates that the
experiment with spectacles, these universals
Since its inception, the concept of ecosystem
construction that this process can be better
through ecological and anthropogenic processes
operational and generative processes.
The
subject is clearly the originator of space. This
are common to all those with similar perceptual
services has evolved and been adapted into an
understood. He summarizes earlier models (e.g.
factors into landscape architecture in major, yet
concept of site is simultaneously erroneous and
is explicated quite clearly in Dan Hoffman’s
faculties. Frascari takes this beyond mere optical
economic model, wherein such services are
Thompson et al 1990) in his discussion of shifting
unrealized ways, the corporeal specificity of site
advantageous. The term site may also conjure
summation (Hoffman 1994) of the experiment
perception, and aligns his research with the
monetized, and their values estimated through
perspectives of nature, and the relationship
is also a crucial component.
a conceptual ground, a locale that is both
in which he describes the inverted world image
imaginative and symbolic, seeking to establish
various models or market surveys (e.g. Boyd and
of these perspectives to ecology.
immaterial yet phenomenologically perceptual.
perceived by the subject wearing the spectacles
a
Banzhafa 2007, Costanza et al 1997, Loomis
discussion encompasses far more than ecology,
Each has its own, inherent, specificity.
as gradually righting itself—that is, over time, the
production.
2000).
Given certain economic weighting,
it sites the discipline within a socially constructed
brain, correlating its visual perception with its
they are sometimes even traded in the market
matrix, subject to many of the same cyclical
experience of gravity, ceases its habitual inversion
14
15
social
process
of
transference
and
While this
(e.g.
nature,
services).
resilience, While
Merleau Ponty (1962) also
non-normative
standard
in
architectural
Heideger, Ponty and Frascari each demonstrate
a phenomenal quality of site, the predominance
(ibid) also cites Koolhaas’ and Frampton’s early
At Woodland cemetery, ground is clearly a critical
field. However, this shift implies a prerequisite
1896), which allows him to begin to play with
discipline of landscape architecture and its
of bodily experience in our perception, and the
calls for a turning to landscape, citing Peter
component, both conceptually and corporeally.
experiential obligation.
Without the traditional
the polemical juxtaposition of these the two
reading of site. By erasing the singular vignette
extensive, cosmological matrix in which such
Rowe’s Making a Middle Landscape (1991) as
At Mill Race Park, ground is a shifting concept
tectonic detail or component (e.g. a cast-iron
terms landskip and landschaft, and their implicit
from
experiences are had. These aspects of site are
the forerunner in the call to just public space.
that reveals not only the potential programmatic
framed bench looking out onto an Olmstedian
imagery to conjure new forms of graphical
contemporary drawing and image production
typically not considered within the sciences, but
However, the scale that these writings operate
inhabitations typical of a public park, but also
pastoral view), such perceptual experiences
representation.
This allows Corner to largely do
acknowledge the multiplicity of both physical and
figure enormously within landscape architecture.
at, and the projects they seek to validate (e.g.
the shifting states of a natural flood plain
may link the body—both conceptually and
away with the crutch of the pictorial collage, thus
conceptual vantage points within the landscape.
Fresh Kills), are developed at such scales that
landscape, inundated and revealed.
phenomenologically—to the landscape, scenically
averting the reassertion of the latent picturesque
As such, landscape representation continues to
While such texts have been celebrated in several
details are sometimes minimal.
This tendency
goes on, echoing Heidegger, to cite Bachelard’s
(landskip)
(landschaft),
in representation. In some ways, the exploration
reinforce the relationship of landscape design as a
architectural treatises (e.g. Libeskind 1992,
towards the minimization of the detail, could
explication of the attic and the cellar, as two
(after Corner 1990). Corner (ibid) explores this
of this idea, documented in Taking Measures
mirror of urban hermeneutics. That is, landscape
Perez-Gomez & Pelletier 1997), the inclusion
be perceived as a viable strategy of departure
structural and simultaneously poetic components
possibility in his collages, departing from physical
Across the American Landscape, (Corner &
has traditionally been conceived as an anti-
of the body in space has largely remained an
from modernism, such as in Van Valkenburgh’s
of the archetypal house that unify earth in sky.
descriptions
MacLean 2000) approaches Smithson’s concept
dote to urbanity. However, the incorporation of
architectural concern, seldom entering into the
larger projects. For example, compare Mill Race
Interestingly,
Bachelard
assembled perceptions of site, thereby combining
of non-site.
In so doing, Corner develops one
process-based diagrams and open-set constructs
emergent discourse of contemporary landscape
Park (Van Valkenburgh 1989-1993) to Asplund
indicates that the cellar is “an antidote to its
the contemporary mapping with the philosophical
proposition of a graphical matrix similar to that
of indefinite outcomes (landscapes) departs
theory, especially landscape urbanism (but see
& Lewerentz’s Woodland Cemetery. While both
inhabitant’s estrangement from the world” (p67),
positions of Heidegger, Ponty and Frascari
described by Pollak (2007) as “multiple forms
from this urban-mirror structure, and begins to
Coner 1999).
Writers such as Berger (2008),
feature similar topographical themes, Woodland
and perhaps a parallel may be drawn between the
discussed above.
of documentation [that] interact dynamically to
address representation of landscape in its own
Corner (2000), Czerniak and Hargreaves (2007),
cemetery contains elements at multiple scales—
absence of the tectonic detail and the revealing of
represent a site (p99). Site may be reinterpreted
right, independent of urban tropes.
and Bélanger (2009) among others, have focused
both architectural and landscape, that Mill Race
the presence of the subterranean, or earth-based
their thinking on largeness (e.g. Koolhaas). This
Park does not.
natural processes.
Dripps’
reading
of
Dripps
2.2
and
of
geographically
site
to
phenomenologically
Site, Scale, and Representation
primary
mode
of
representation,
not as a collage of images, but as a collage of interpretive techniques.
The inclusion of ecological theory in landscape
In Recovering Landscape, Corner (1999) develops
is due in part to the shortcomings of modern
the
architecture is now being projected from the
of
Robin Dripps (2005) in her essay “Groundwork”
Strategies of detail minimization can shift one’s
the idea of the eidetic image—an elaboration
Collage, then, can also challenge the latent
landscape back into the urban, instead of the
modernist planning (Waldheim 2006a). Waldheim
discusses the structure and materiality of ground.
perception from the tectonic to the temporal
on Bergson’s conception of image (Bergson
prevalence of the picturesque still extant in the
reverse, and is tantamount to a theoretical shift
architecture,
and
developing
critiques
16
17
that begins to erode the historical urban/natural
Cage in the 1950s and to Smithson in the 1970s.
and proportion are equated with control—
the structure, in this case, the angle of repose—
served a larger goal.
dialectic. While it has been noted that landscape
These examples serve to round out the idea of
by the artist—and a the reinforcement of
an
the angle at which soils may resist sliding. The
constitute a mapping of an abstract geography.
urbanism neglects a certain level of detail, it
indeterminate process separate from that of the
establishment. The informe also implies a natural
mass and composition of the asphalt possesses
They are a product of the limit of the camera
brings qualities of landscape—both conceptual
ecological sciences.
affinity for entropy—for the natural deformation
different physical properties than that of the
frame, but also a conceptual re-scaling of form.
of ideal form.
These concepts of process,
native soils. Likewise, it is also dumped from a
By mapping these assemblages of minerals
approaches as well as ecological and phenomenal
Smithson’s photographs
ones—to bear on the urban setting, often
The evolution of art from a creative act to an
including entropy, configure many of Smithson’s
tilting truck bed, which lends acceleration. Here,
(rock placements), Smithson begins to question
dissolving particular historical dialectics. This is
autonomous process required the displacement
major works.
the juxtaposition of asphalt against native soils
the conceptual limits as they function within
most clearly seen in the built works of landscape
of the creator—the subject (and thereby the
accentuates the static limit—the angle of repose—
representation, calling into question not the form,
urbanism, such as Downsview Park, and Freshkills.
object)—in order to emphasize the
process
Smithson’s Partially Buried Woodshed 1970 or
of the existing conditions, while re-temporalizing
but the presentation of that form. However, while
However, the emergence of low impact design
with which the object was brought forth. The art
Asphalt Rundown 1969, are simple but rigorous
the slow, entropic process of erosion that has
portending to exceed the physical limit of the site
strategies for stormwater management also
theoretician Rudolf Arnheim (1971) considers the
processes used to invoke entropy while negating
gradually shaped the abandoned gravel quarry
through photography (mapping), a corporeal trace
imply similar, though unexpressed, conceptual
role of process in early Dadaist art, where the
form. In the Woodshed case, collapse is hastened
into which the pour was made.
of the means of constructing the representation
renegotiations.
process superseded the product, noting Jean
through the addition of soil, piled until the limit
Arp’s paper drops of the 1920’s where controlled
is reached, and the structure fails.
While this
Smithson’s smaller works, such as his Hypothetical
distinct from Corner’s mappings (i.e. drawings),
randomness produced both affect and effect.
project contains other overtones commensurate
Continents 1969, and Mirror Displacements 1969,
in that the scales of Corner’s drawings are vast
He traces this externalization of the artist from
with historical events at that time at Kent State
raise issues of the limit as well (Smithson & Severi
enough that the body is invisible, and perhaps
The erosion of the objective, tectonic detail
the product to John Cage’s work which coupled
(where the woodshed was located), it also raises
1997).
irrelevant, in the privileged aerial vantage point.
through the emergence of subjective processes
chance and random elements with traditional
the notion of the limit.
In this work, process
limits, rather than physical or mechanical.
discussed above has several parallels in the art
artistic craft.
defines limit—an intangible but verifiable reality,
Smithson regularly documented these works
world of the mid Twentieth Century. These can
negate form all together, as in Bataille’s informe
as real as form, but formless nonetheless.
In
photographically. While these photographs could
be traced from the Dadaists in the 1920s through
(Bois & Kraus 1997), where symmetry, hierarchy,
Asphalt Rundown, the limit is incorporated into
transpose works into the gallery setting, they
2.3
Site, Scale, and Process
Such process-based works may
18
is embodied within its construction. This is quite
However, these limits are conceptual
3.0
Industrial Ecology
The DIG STUDIO project is specifically
framed around the question of industrial ecology and the fate of post-industrial landscapes. While there are wide variations among sites that may be classified as post-industrial, the contaminants within the subsurface are often derivatives of closely related industrial and chemical processing. An understanding of this chemical genealogy can contribute to a more thorough reading of both individual sites as well as the larger post-industrial landscape in which they are often set. The legacy of synthetic industrial contaminants that typically persist in an enumerable number of post-industrial sites can be traced back to the evolution of chemical engineering.
This
evolution began with the textile industry, but soon permeated every mode of production. By 1835, the steam engine and the cotton gin had both
19
contributed to the formation of a newly expansive
chemist William Henry Perkin, develops the first
of nitrogen (namely saltpeper from Chile) were
styrene and other polymers, and usher in the
produce kerosene for lamps and fuel for warships
textile industry in Europe and in the States. The
analine dye, based on coal tar—analine purple.
in short supply.
By 1913, BASF innovated the
advent of early plastics (BASF 2005c), and by
(ibid).
cotton gin allowed previously unprofitable strains
This discovery led to the development of an
manufacturing of ammonia, a substance rich in
1936, the first synthesized rubber, ‘Buna,’ (ibid).
British
of cotton to be processed economically, thus
entire line of analine dyes, and the development
nitrogen, by extracting N from the atmosphere,
While other products such as U46 pesticide and
German vessels had already set the stage for
leading to the generation of a new industrial-
of an industrially-based dye supply capable of
and producing 36k mT of ammonium sulfate at
Styrapor (Styrofoam packaging) were produced,
the development of the petrol industry by WWI.
agriculture landscape. The production of cotton
sustaining the burgeoning textile industry (BASF
their new, high pressure facility. After the first
by 1953 BASF was refining its own oil for the
However, naptha (gasoline) is only one byproduct
in the southern states, for example, increased
2005a). The lack of color fastness, however, led
world war, high pressure technology lead to the
production of polyethylene, one of its most
of crude oil refinement. Other products include
more than 300% between 1790 and 1835, from
to the development of other synthesized dyes,
synthesis of methanol in 1923, freeing industry
successful products.
industrial lubricants, asphalt and sulfur. Synthetic
3,000 bales to 1 million (Lemelson Center 1998),
such as Alizarin, eosin, and auramine.
And in
from the limits of tree-based alcohol. Methanol
and 75% to 85% of the cotton produced in the
1876, Henrich Caro, of BASF-- Badische Anilin-&
contributes to the production of formaldehyde
What BASF leaves out of its history, however, is
southern states was consumed by Britain or the
Soda-Fabrik—also synthesizes methylene blue,
and urea, and ultimately plywood in 1931 (BASF
the co-development of the refinery. Despite the
States (Wright, 1971).
The increase in newly
from coal tar. Subsequently, BASF also acquired
2005c).
At the same time, beginning in 1913
1907 acquisition of the Auguste Victoria coal mine
In addition to the preliminary products of
available raw cotton required the innovation of
the license to produce artificial indigo dye as well.
and ending in 1927, gasoline was synthesized
in Marl, Germany, by BASF, Bayer and AGFA, and
refinement, other petrochemicals were eventually
from coal using hydrogen and high pressure
other advances in high pressure chemistry, the
extracted through distillation or catalyzation.
The recognition of depleted soil in Europe,
technology.
Interestingly, this idea was put
US was able to out-compete Germany with more
These
Quantities of traditional organic materials used for
decried by Sir William Crookes in Britain in the
forward by the States prior to WWI, with the
advanced petroleum refinement technology. This
benzene, and xylene, which serve primarily as
fiber dying, such as madder and indigo, became
early 1900’s in his lecture ‘The Wheat Problem,’
anticipation that existing reserves of petroleum
lead to higher performing fighter planes fueled
feed stock for additional stages of production and
insufficient to supply the exponential increase in
(BASF 2005b) set in motion a new development
might soon dry up, and it has also come into the
by higher octane gasoline in WWII, (Williamson &
refinement, comprising a large list of additional
demand for dyes. Readily available substitutes
in chemical engineering.
spotlight recently with the US Military’s spending
Daum 1959), and in turn the world’s first refinery
petrochemicals and legacy toxins.
like sulfuric acid, soda ash and chlorinated lime
production had gradually eroded fertile soils
considerations and allocations.
By 1929, high
industry. However, the first refinery was not build
are employed in processing. In 1856, the British
and their nutrient base, and organic sources
pressure acetelyne was being used to derive
in the States, but in Britain, in 1862, in order to
new procedures for drying, dying, and weaving.
20
Conventional wheat
The performance of hydrocarbon-fueled naval
vessels
against
coal-powered
rubber was another major development stemming from the refinement process.
include
ethylene,
propylene,
4.0 Closure
While the precise relevance of each
topic or subcategory to the design-phase of DIG STUDIO has not been made entirely explicit, the ground for multiple trajectories has been established. However, certain traces are worth acknowledging here. The role of indeterminacy, in both outcome and causation was a major factor in the design phase. Nevertheless, indeterminacy
toluene,
was consistently challenged by the relevance of site components and archeology, such as buried pilings or disused railroad tracks. Likewise, there was always a tension between the exact scale of landscape (e.g. the Columbia River Basin) and the somatic experience of walking along the Willamette River’s armored banks. Representation, collage, and drawing, in the end, remained subject to projection systems, long-phase feedback loops, and process-based design, though this was not the initial intention. The literature reviewed above
21
suggested trajectories and intersections, as well as gaps and interstitial possibilities for DIG STUDIO.
22
23
Alberti, M., (2008). Advances in Urban Ecology:
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Measures Across the American Landscape. Yale
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Brand, F.S. and Jax, K., (2007). Focusing
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the Meaning(s) of Resilience: Resilience as a
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Infrastructure. Landscape Journal 28:p1–09.
Ecology and Society 12(1): 23.
in Contemporary Landscape Architecture.
Parks. Princeton Architectural Press, New York.
the Era of Fertilizers. BASF Historical Milestones
Princeton Architectural Press, New York.
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The Body, Landscape, and Toxic Exposures.
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29
ECHNOLOGY & TECHNIQUES
HYTOREMEDIATION
1
PHYTOREMEDIATION
0.1 Intro Phytoremediation is the process of using plants to remediate
TECHNOLOGY & TECHNIQUES
ground-based contaminants within the shallow subsurface. Phytoremediation was anticipated to be a major tactical operation for DIG Studio, and as such we conducted an intensive review of
contemporary literature pertaining to phytoremediation
technology, both its biological mechanisms and its limits. Under the direction of Professor of Forest Sciences Sharon Doty, (PhD UW-SEFS) we reviewed a total of ten publications from the recent scientific literature—five concerning organic compounds, and four concerning heavy metals—in an effort to more accurately inform our design process. The contaminant inventory for our selected site, The Port of Portland Superfund Site, contains over 89 different contaminants, 29 of which were identified by the EPA as having potential pathways for human contact or ingestion.
02
03
0.2
Conventional Remediation in Brief
The advent of chemical dyes in the mid-19th century, designed to accommodate the growing demand for textile processing, lead the way for high-yield catalyst reactions, high pressure technologies, and crude oil refinement. With the switch from kerosene to diesel, the refining processes gradually lead to the development of numerous hydrocarbons, petrol additives, plasticizers, and volatile organic compounds used throughout modern industry. The legacy of these processes has often been left in the ground in the form of toxic plumes, the contents of which slowly leach into ground water, or find their way to the surface through various pathways. The General Accounting Office currently lists over 425,000 brownfield sites in the US (ELI 2012) alone, and of those there are an estimated 12,000 that qualify as superfund sites, exceeding the Hazardous Ranking System of 28.5 (ICMA 2002). The numbers for European sites are even higher (Doty 2012). While the exact amount of funding spent on monitoring and clean-up is unknown, it is estimated to be between $6-$8 billion annually in the US, and over $25 billion globally (ibid).
Numerous industrially-intensive technologies have been developed to remediate such sites. Damera & Bhandari (2007) list some conventional techniques: •
Free product recovery, where leaching nonaqueous liquids
are recovered in wells or excavation trenches; •
Pump and treat, where contaminated groundwater is
pumped to the surface, treated, and re-injected into the ground; •
Soil vapor extraction, where a pressure gradient is generated
in the saturated area and volatile compounds are captured at the surface; •
Air sparging, which involves the injection of air below the
saturated area that in turn removes chemicals while it rises to the surface where it is captured; •
Ground water circulation, which employs sub-surface
circulation through several specially designed wells where the contaminant is treated through a series of screens. •
Induced fracturing and soil heating, which are often used
in conjunction with soil vapor extraction to remediate chemically saturated sites (ibid). While generally highly effective, each of these technologies involves
04
extensive
site-specific
05
data
generation,
expensive
specialized machinery and highly customized infrastructure. The
& Brar et al 2007, after Schwitzguebel et al 2005). Phytoremediation
use of such techniques explains some of the costs associated
seeks to optimize the “selective uptake capabilities of plant
with remediation processes. For example, over $22M dollars was
root systems, along with the translocation, bioaccumulation,
spent on a single site, known as McCormic & Baxter, in the Port
contaminant storage and degradation capabilities of entire plant
of Portland Superfund Area over a ten year remediation process,
systems,” (Champagne 2007 p292, after Suthersan 2002). More
leaving behind a barb-wired brownfield with continued seepage of
recent work in phytoremediation focuses on the optimization of
toxins into the Willamette River. Though this site is highly desirable
endophytic bacteria—root colonizing bacteria—to degrade ground
to nearby Portland University, the stigma of the site’s toxic legacy,
contaminants. While plants may bioaccumulate heavy metals and
together with unknown chemical pollutants, prevents the University
other toxins, selected bacteria are capable of breaking down a
from utilizing their new property. Once the pollutant sources are
variety of organic chemicals, and converting their components
removed, phytoremediation offers a low-cost technique to address
into metabolic elements useful to the host plant, such as carbon
the in-ground contaminants that remain.
and nitrogen. While these techniques require much of the same baseline data as conventional remediation techniques, they may
1.0 Organics
be refined and tested in a lab setting. Likewise, once established, plants require less minute oversight than mechanical operations.
Research over the last decade has extensivley investigated several
A literature review of current research into endophytic bacteria
alternative techniques to remediate brownfield and superfund
derived from various strains highlights some recent developments.
sites. These techniques involve the use of biological treatments including bacteria, fungus, and plants. The application of plants for remediation is known as phytoremediation, which uses plants and their associated microbiotic processes to clean soil and water (Blais
06
07
1.1
able to bioaccumulate both toxins in their root systems, preventing
RDX & TNT
the redistribution of the toxins by herbivory or other vectors.
Rylott & Budarina et al (2011) investigated the use of transgenic plants in the breakdown of two explosive compounds, often found together in detonation sites, RDX and TNT.
RDX—hexahydro-
1,3,5-trinitro-1,3,5-triazine—is classified as a potential human carcinogen by the EPA and typically leaches into groundwater (ibid). While it is often readily absorbed by plants, it is rarely broken down (ibid). However, the authors indicate that several bacteria have been identified that do break down RDX. However, because RDX is often found in combination with TNT—a high phyto-toxin and human carcinogen, phytoremediation of RDX is often impossible. The authors proceeded to combine strains of the bacteria Rhodococcus rhodococcus, which is known to degrade RDX with strains of Enterbacter cloacea, a bacteria known to tolerate and detoxify TNT. Strains of the resultant bacteria were tested in the lab for their tolerance and degradation of RDX+TNT, then inserted into Arabidopsis thaliana (mouse-ear cress), a highly studied and genetically-sequenced member of the mustard family (arabidopsis.org). Soil tests with 250mg/kg TNT and RDX concentrations confirmed that the transgenic Arabidopsis were 08
However, the authors conclude that based on the limited root depth of Arabidopsis plants that perennial grass species, such as Pascopyrum smithii, Elymus trachycaulus and Agropyron fragile, might be preferred on-site for their fire resistance and tolerance of heavy machinery.
1.2
Trichloroethylene & Poplars
Weyens
and
Van
Der
Lelie
et
al
(2009)
investigated
phytoremediation of a trichloroethylene (TCE) contaminated site through an in-situ inoculation of poplars with Pseudomonas putida W619-TCE.
TCE is a volatile organic compound often
used as a solvent in manufacturing, and in PVC manufacturing, paint thinners, and sometimes household paint as well. While trichloroethylene (TCE) can be absorbed by plants, it is often subsequently evapotranspired into the ambient air by the plant. This serves to simply relocate the contamination, rather than degrade it. This is also a typical result of conventional remediation techniques such as air sparging.
09
The experiment employed
Populus deltoides×(Populus trichocarpa×Populus deltoides) cv
a non-competitive relationship where the inoculate may succeed
Grimminge, which were planted downstream and perpendicular to
in colonizing the rhizosphere without significant inhibition from
the TCE plume. Evapotranspiration of TCE was measured 2 years
existing native bacteria.
after planting. A selection of poplars was then inoculated with Pseudomonas putida W619-TCE, a bacteria developed through
1.3
BTEX & Poplars
horizontal gene transfer from naturally occurring and recently sequenced P. putida W619. According to the authros, P. putida
Barac and Weyens et al (2009) investigated the effectiveness of
W619 is closely related to P. putida KT2440, a recognized and safe
two poplar hybrids in the phytoremediation of a BTEX plume in
bacterial strain. Evapotranspiration of TCE in inoculated poplars
Belgium. BTEX is a petroleum distillate, and often associated
was 9 times less that of the control trees. Post-inoculation analysis
with fuel additives.
determined that other, naturally occurring endophytic bacteria—
conditions, evaporation is often restricted.
Pseudomonas and Frigoribacterium spp.—were also capable of
migrate along groundwater pathways, contaminated the water as
breaking down TCE, a function attributed to the bioaugmentation
well as the soil. As this plume was located 4-5m below grade,
of the rhizosphere with Pseudomonas putida W619-TCE, as this
poplars (and their roots) presented a viable delivery system for
capacity was not found in the noninoculated poplar samples.
BTEX-degrading bacteria. Two poplar hybrids were selected for
Notably, these native strains lost their TCE degradation capacities
planting, in part due their fungal resistance: Populus trichocarpa ×
after 20 generations of breeding in non-saturated conditions
deltoides cv. “Hoogvorst” and “Hazendans.” The trees were planted
(without TCE), indicating that they returned to their natural, pre-
reciprocally, and perpendicular to the BTEX plume migration, in
inoculated states.
This parallels similar discoveries by Barac
9 rows of 30 trees each, at 7m centers. The trees were sampled
(2009), reviewed below. Also, the horizontal gene transfer of the
at intervals, beginning 13 months after planting. It took nearly
inoculate bacteria strains to the native bacteria strains indicates
three years for the roots to reach the plume, but after they did,
10
11
While volatile, when located in subsurface BTEX plumes will
core samples indicated that the plume was receding. Additionally,
Lupine (Barac & Taghavi 2004).
The implication of both the
tissue samples of Populus trichocarpa Ă— deltoides cv. “Hoogvorstâ€?
above experiments is that naturally occurring endophytic bacteria
indicated that naturally occurring BTEX-degrading endophytic
do have the capacity to breakdown BTEX, they can be isolated,
bacteria had increased significantly, and that horizontal gene
grown, and re-inoculated into host plants.
transfer of toluene-degrading plasmids had occurred within the native endophytic strains of the poplar roots. Samples within the
Naphthalene is a polyaromatic hydrocarbon used in the
plume indicated a significant increase in this capacity. However,
production of plasticizers, insect repellents, pharmaceuticals
and importantly, once the plume receded (once the BTEX was
and dyes (Germaine & Keogh et al 2009).
degraded) the populations of these bacteria also receded, with
quickly in the ambient air, it does so slower when in combination
colony-forming-units (CFU) dropping to undetectable levels.
with other PAHs in sub-grade anaerobic settings. Likewise, the
While it degrades
presence of Naphthalene can prevent the phytoremediation
1.4
BTEX & Endopytic Bacteria Innoculate
of other PAHs (ibid), though this is a point of some contention (Doty 2012). Germain and Keogh et al (2009) investigated the
Moore and Barac (2006) also studied the potential for naturally
use of an endophytic bacteria inoculate (Pseudomonas putida
occurring endophytic toluene-degrading bacteria isolates to
VM1441(pNAH7) in the phytoremediation of Naphthalene. They
cultivated and re-innoculated into poplars, thereby increasing
cross-bread endophytic P. putida VM1441 with soil-based P. putida
the response time of poplar-based phytoremediation. This is of
G7(pNAH7) to produce the inoculate, and used pea plants for
concern because federal regulations often stipulate a certain time
their typically low rhizosphereic CFU characteristics as well as
frame for proof of effectiveness in alternative, non-prescriptive
their easily germinated seeds. Their findings indicate that their
clean-up measures (Doty 2012).
This study emulated similar
inoculations encouraged increased rates of both transpiration
results involving the re-inoculation of Lupinus luteus L. - Yellow
(10-40%) and degradation (40%). The inoculate also added to the
12
13
pea plants’ naphthalene resistance. Inoculated plants were able
tolerance and degradation of ATZ. They identify three distinct
to tolerate doses of naphthalene up to 100mg/kg, but at doses of
mechanisms for ATZ tolerance, and eventual degradation: genetic,
200mg/kg the cessation of germination was observed.
enzymatic and non-enzymatic. While the exact mechanics of these processes are beyond the scope of this thesis, their extensive
1.5
Atrazine & Rye Grass
analysis supports their hypothesis regarding these mechanisms, and suggests further research into the use of rye grass in the
While endophytic bacteria are often critical in the degradation of
phytoremediation of ATZ.
organic compounds, certain plants present integral mechanisms Lolium mutiflorum (rye
While endophytic bacteria contribute to the degradation of organic
grass) is one of these. It has several advantages in the breakdown
compounds such as RDX, TNT, TCE, BTEX, and some PAHs, their
of Atrazine (ATZ) in agricultural areas. It does not compete with
capacity to deal with inorganic compounds such as heavy metals
the primary crop, and it is typically used in rotation with corn,
is [negligible]. Phytoremediation of heavy metals often results
sorghum and sugar cane (Merini & Bobillo et al 2009). Likewise,
in bioaccumulation in the plant of the target metals, requiring
L. mutiflorum is capable of germinating in the presence of ATZ—a
different management strategies.
photoshynthesis-inhibiting pesticide. While ATZ is readily broken
inorganic compounds will be discussed next.
for tolerating or degrading pollutants.
The phytoremediation of
down by soil-bound microbials, the quantities in which it is often applied exceed the natural capacity of the soil and saturation
2.0 Metals
insues (ibid). Mereini and Bobillio et al (2009) studied the potential of Lolium mutiflorum for use in phytoremediation of ATZ
The phytoremediation of
in agronomic soils, and in conjunction with existing agricultural
plant processes and pathways than those required for organic
cultivation. They studied the in-plant pathways that enabled the
compounds.
14
heavy metals relies on different
While endophytic bacteria contribute to the
15
degradation of organics, heavy metals present no potential break
microbial activities within the plant root structures allow metals to
down pathways as they constitute their elemental form. Therefore,
bind with soil particles, thereby reducing their potential release into
phytoremediation of heavy metals relies on bioaccumulation—the
groundwater migration pathways; phytofiltration – phytoextraction
extraction of metals from the ground by the plants root network,
by water-based plants (Sarma 2011). While hyperaccumulators
and the storage of those metals in the plant’s tissues. Plants that
can absorb impressive quantities of localized heavy metals,
readily accumulate heavy metals are known as hyperaccumulators,
certain limitations exist. Phytoremediation is typically slower than
because they are able to accumulate and tolerate metal
conventional methods, and the target metals must be in a bio-
concentrations up to 100 times that of other plant types (Baker
available form, that is, not linked to other molecules that prevent
& McGrath et al 2000).
As a phytoremediation technique,
initial absorption (ibid). Also, water-soluble metals can pass by
bioaccumulation also requires different management strategies
the root system entirely (ibid). Additionally, metals are frequently
from organic phytoremediation, as the concentrated metals in the
found in conjunction with other metals and organic compounds
plant tissues typically require sequestration and recovery to remove
such that some metals may be toxic to certain hyperaccumulators
them from the environment completely. Generally, harvested plant
and prevent effective absorption of the target metal(s). Among
matter can be reduced to ash through combustion, which yields
the approximately 500 hyperaccumulators identified, each plant
a small quantity of metals which can be handled and transported
presents its own metal transfer factor from soil (TFS) rate (ibid).
more efficiently.
Hyperaccumulators operate through one of
The depth at which target metals are located can pose a limitation
the following mechanisms: phyoextraction – metals are absorbed
for certain types of plants, especially grasses, whose roots extend
through the roots and translocated to harvestable tissues such
only several inches below grade. Several current studies investigate
as leaves and stems; phytovolatilization – extracted metals are
the performance of different hyperaccumulators.
released into the atmosphere once they are translocated from the ground into above-ground plant tissues; phytostabilization –
16
17
2.1
Heavy Metals, Willow & Poplar
Mrnka & Kuchar et al (2011) studied the effects of endo- and ectomycorrhizal fungi inoculation on bioaccumulation in Salix alba L. and Populus nigra L. Both plans present opportunities for bioaccumulation of metals located beyond the reach of shallow root systems, and offer tolerances to multiple types of metals. The paper explored the effects of inoculation to the production of biomass and bioaccumulation of Cd, Pb, and Zn. The authors identify several beneficial attributes of both plants, namely their high biomass production, extensive root systems, their high tolerance to heavy metals, and high TFS, and identify several performance differences between each species and their innoculate counterparts.
The various permutations of host and inoculate
presented multiple results, indicating that certain combinations are more effective for certain metals (arbuscular mycorrhizal & P. nigra for Pb & Fe; and ectomycorrhizal & S. alba for Zn & Cd). Additionally, certain mycorrhizal inoculates either stunted growth or retarded bioaccumulation in either P. nigra or S. alba. While the experiment’s results were mixed, several results proved promising for continued study, however the authors acknowledge that the 18
effects of multiple relationships between mycorrhizal fungi and plant hosts, as well as substrate contamination levels are difficult to isolate.
2.2
Arsenic & Chinese Brake Fern
While multiple heavy metals are typically found in conjunction with one another in industrial areas, heavy metals are sometimes found to be singularly isolated in natural sites. Arsenic is one such metal that is can be found in association with ground water. Arsenic (As) can be found in multiple forms, including arsenate and arsenite. Because arsenate closely resembles phosphate, it is often taken up by organisms, resulting in toxicity. Ye & Khan et al (2011) investigated the potential of Pteris vittata (Chinese brake fern) to reduce the uptake of arsenate in rice grown in SE Asia. P. vittata is a recently discovered hyperaccumulator of As, first identified in 2001 (Ma & Komar et al 2001). Anaerobic soil conditions allow for the leaching of naturally occurring arsenic into ground water and recently dug irrigation wells. The authors conducted their tests in laboratory conditions, but demonstrated that P. vittata could in fact reduce arsenate absorption in rice by
19
pre-emptive bioaccumulation in the fern, which can absorb up to 26% of soil-based arsenic, resulting in a concentration level 10 times higher than the contaminated soil. Xie & Yan (2009) also note that arsenic removal efficiency could be enhanced by the addition of low amounts of phosphate to the soil, though they are also unclear about where, exactly, arsenate is changed to arsenite (ibid). However, the 2011 experiment also presents new questions, such as the post-phytoremediation reduction of rice grain size, and the mortality rate of other rice plants. They propose that there may be some complications due to nutrient depletion by the ferns, or from root remnants in the soil, after fern extraction, that interferes with rice plant development. It’s also possible that the soil itself is depleted, and that arsenate absorption by rice was compensating for an overall lack of bioavailable phosphate. It’s noteworthy to also mention that P. vittata doesn’t readily grow in all climates, as it was trialed at one point in Puget Sound for phytoremediation of the Tacoma Smelter arsenic plume (Doty 2012).
2.3
Mercury & Rushes
Mercury is another naturally occurring heavy metal that is often found in larger isolated concentrations.
While natural sources
of mercury emissions include geologic activity and naturally enriched substrates (Marques & Lillebo et al 2011), the majority of toxic methyl-mercury pollution can be traced to fossil fuel burning, mining, and industrial activities including cement production. Marques and Lillebo et al (2011) investigated the capacity of salt water marshes to auto-remediate mercury. While their paper presented an ecosystem services-based argument for the preservation of saltwater marshes, it also elucidated some naturally occurring pathways for phytoremediation of mercury. The authors identified Juncus maritimus (sea rush) and Scripus maritimus (bulrush) as natural bioaccumulators of mercury. Their investigation revealed that mercury was typically sequestered in the roots of S. maritimus below the surface, rather than in the short-lived leaf tissues. Similar sequestration findings by others are also cited for Cd, Pb, and CU in Spartina maritima. However, the below ground Hg (rhizosediment Hg) is more dynamically exchanged, and the authors therefore conclude that J. maritimus
20
21
actually provides a higher sequestration capacity. Additionally, by
blooms typically appear at the mouths of large river systems,
concentrating the mercury in its leafs, J. maritimus allows for the
where nutrient concentrations are highest.
phytovolatization of mercury back into the natural atmosphere. Atmosphereic dilution in this case is generally considered the best
Lu and He (2010) investigated the potential of Pistia stratiotes
remedy, as low concentrations of mercury are found in existing
(water lettuce) to phyoremediate phosphorus in marine harbors.
natural cycles. However, exposure to UV light can result in the
While potentially highly invasive, in certain settings, their 2
conversion of elemental mercury to ionci-mercury, preparing
year study suggest that moderate improvements were possible
it again to renter the environment. This suggests that carefully
(between 7-51% reductions in nutrient levels). A similar, but much
harvesting a portion of the total fronds of degenerating J. marimus
shorter study, investigated Eichhornia crassipes (water hyacinth)
may provide a way to sequester mercury and may be one way to
as a potential phytoremediator of N and P in fresh water systems
remove excess from the environment.
(*source*). Like water lettuce, it is also highly invasive, and requires a high nutrient load to flourish, but under such conditions, it can
2.4
Excess Nutrients
double its biomass in 6-15 days. While shorter, the experiment provided similar, though less certain results. However, due to the
Lastly, excess nutrient run off has been shown to be the cause of
highly invasive potential of both plants, it may be best to consider
eutrophication in over 400 systems across the globe. Nitrogen
more locally adapted, native plants for phytoremediation of excess
and phosphorus are readily applied as fertilizers in industrial
nutrients, or on-site treatment and BMPs at agricultural sites.
agriculture, and have been identified as the source for over 245,000 sq km of algal blooms.
These blooms occur mostly
along the eastern seaboard and coastal Europe, though they are beginning to appear around Africa as well (NASA 2012). These
22
23
is also noteworthy that specific species of plants may be well
3.0 Conclusion
adapted to certain geographical locations, and mal-adapted to
In both organic and inorganic phytoremediation, the applicability of specific plants, or special cultivated varieties of each plant, are extremely specific to the target toxin.
While some plants
may phytoremediate certain substances, other chemicals often found in conjunction with the target substance may interfere with phytoremediation, and produce results not predicted by laboratorybased testing. Field testing may also include other unforeseen variables such as native micro-organisms that may compete with endophytic and mycorrhizal innoculations, thereby reducing the efficacy of such treatments.
Likewise, bioaccumulation,
sequestration, or degradation processes are not only different for each plant, but often benefit from precise, yet preliminary research into the production of appropriate micro-organism inoculates. The development of inoculates and the combination with host plants presents a wide field of variability, complicating the potential for initial full-scale success rates. At the same time, polluted sites often contain desirable partnerships between host plants and micro-organisms already adapted to specific toxins, and are readily being further optimized for phytoremediation. It 24
others. Or worse, they may be invasives.
The costs for phytoremediation are often several orders of
magnitude less than conventional remediation techniques. However, regulations often place an untenable burden on phytoremediation by requiring proof-of-efficacy within 3 years. This time limit is one of the main drivers behind current research to improve the efficiency of phytoremediation. This drive may also, inadvertently, lead to the creation of undesirable GMO strains, though these strains may not outlive natural species once their toxic nutrient sources are depleted. In the end, phytoremediation remains an extremely compelling alternative to conventional techniques as it awaits further successes in field trials.
4.0
Design Implications
DIG studio employed several of the techniques discussed
here, and made provisions for the inclusion of others based on the literature. The array of contaminants present at the Port of Portland Superfund Site greatly exceeds the capacity of the literature.
25
However, pending further developments in biotechnology and phytroremediation, many of the techniques discussed above may be adapted to new hybrid species or different inoculates. At the McCormic & Baxter site. Many of the legacy contaminants within the larger Superfund Site fall into larger categories of chemical families that may be treated with similar techniques. However, as noted above, the presence of some chemicals can initially hinder the phytoremediation of others. This implies a mixed approach that utilizes both conventional and alternative methods for remediation of contaminants. These are both included in DIG’s tactical archive.
26
27
Germaine, K.J., Keogh, E., et al (2009). Bacterial endophyte-mediated naphthalene phytoprotection and phytoremediation. FEMS Microbio Lett 296, pp 226-234.
Literature Cited Barac, T., Weyens, N., et al (2009). Field Note: Hydraulic Containment of a BTEX Plume Using Poplar Trees. International Journal of Phytoremediation, 11:416-424. Barac, T., Taghavi, S., et al (2004). Engineered endophytic bacteria improve phytoremediation of water-soluble, volatile, organic pollutants. Nature Biotechnology v22n5 May. Baker A.J.M., McGrath S.P.et al (2000) Metal hyperaccumulator plants: a review of the ecology and physiology of a biological resource for phytoremediation of metal polluted soils. In: Terry N., Banuelos G.S. (Eds), Phytoremediation of Contaminated Soil and Water. CRC Press, Boca Raton, FL, USA, pp 85–107. Bhandari, A., Surampalli, R.Y., et al, ed (2007); Remediation Technologies for Soils and Groundwater. American Society of Civil Engineers. Blais, J.F., Brar, S.K., et al (2007). Metal Removal, in Bhandari, A., Surampalli, R.Y., et al, ed (2007); Remediation Technologies for Soils and Groundwater. American Society of Civil Engineers. Champagne, P. (2007). Phytoremediation, in Bhandari, A., Surampalli, R.Y., et al, ed (2007); Remediation Technologies for Soils and Groundwater. American Society of Civil Engineers. Damera, R. & Bhandari, A., (2007). Physical Treatment Technologies, in Bhandari, A., Surampalli, R.Y., et al, ed (2007); Remediation Technologies for Soils and Groundwater. American Society of Civil Engineers. Doty, S. 2012. Class lecture, Jan 4th- Mar 14th. ELI, 2012. Environmental Law Institute, Brownfields Center. http://www.brownfieldscenter.org/big/faq.shtml
ICMA 2002. Brownfields Redevelopment: A Guidebook for Local Governments and Communities—Second Edition. International City/County Mangement Association, Superfund/Brownfield Research Institute. Libor, M., Kuchar, M., et al (2011). Effects of Endo- and Ectomycorrhizal Fungi on Physiological Parameters and Heavy Metals Accumulation of Two Species from the Family Salicaceae. Water Air Soil Pollut 223:39-410. Lu, Q., He, Z.L., et al (2010). Phytoremediation to remove nutrients and improve eutrophic stormwaters using water lettuce (Pistia stratiotes L.). Enviro Sci Pollut Res, 17:84-96. Ma, L. Q.; Komar, K. M. et al (2001). A fern that hyperaccumulates arsenic: a hardy, versatile, fast-growing plant helps to remove arsenic from contaminated soils. Nature 2001, 409, 579. Marques, B., Lillebo, A.I.., et al (2011). Mercury cycling and dwquestration in salt marsh sediements: An ecosystem service provided by Juncus martiums and Scirpus maitimus. Environmental Pollution 159, pps 1869-1876. Mereini, L.J., Bobillo, C., et al (2009). Phytoremediation potential of the novel atrazine tolerant Lolium multiflorum and studies on the mechanisms involved. Environmental Pollution 157, pp3059-3063. Moore, F.P., Barac, T., et al (2006). Endoophytic Bacterial Diversity in Poplar Trees Growing on a BTEX-contaiminated Site: The Characterization of Isolates with Potential to Enhance Phytroremediation. Systematic and Applied Microbiology, 29, pp539-556. NASA, (2012). http://earthobservatory.nasa.gov Rylott, E.L., Budarina, M.V., et al, (2011). Engineering Plants for the Phytoremedia-
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29
tion of RDX in the Presence of the Co-contaminating explosive TNT. New Phytologist 192:405-413. Sarma, H., (2011). Metal Hyperaccumulation in Plants: A Review Focusing on Phytoremediation Technology. Journal of Environmental Science and Technology 4(2): 118-138. Weyens, N., Van Der Lelie, D., et al (2009). Endophytic Bacteria Improves Contaminant Fate in Phytoremediation. Environ Sci Tehcnol 43, pp9413-9418. Xie, Q.E, Yan, X.L., et al (2009). The Arsenic Hyperaccumulator Fern Pteris vittata L. Envrionmental Science & Technology, v43n22, pps 8488-8495. Ye, W., Kahn, K.M., et al (2011). Phytoremediation of arsenic contaminated paddy soils with Pteris vittata markedly reduces arsenic uptake by rice. Environmental Pollution 159, pps 3739-3743.
30
ESTABLISHING A NEW METHODOLOGY
METHOD
01
The Challenge
A new process & approach
DIG STUDIO seeks to establish a methodology for
ENGAGING ENTROPY
methodology
and
our
critique
of
traditional
utilizing entropy as a design tactic. DIG STUDIO
Key characteristics of industrially-modified sites
in general, misunderstood and ignored entropic
remediation methods. Discussion lead to further
began with the premise that design needed new
include degraded maintenance regimes, entropic
systems.
critiques of how we currently define health and
approaches to create healthier landscapes, people
boundaries, and migrating plumes. DIG STUDIO is
and ecologies. Ultimately, this project proposes
particularly interested in patch dynamics of such
Entropy is inherent in our urban and ecological
Health is the combined effects of successive,
new design tactics that engage entropic processes,
sites, such as the interface with industrially modified
systems, our futures are dynamic and indeterminate.
evolving, and indeterminate landscape processes and
incorporates indeterminate outcomes, and allows
sites with multiple urban scalars—social structure
Here, we discover a correlation between entropy and
management strategies on human well being.
for evolving autonomous and informal ecologies.
of cities and their surroundings, direct relations
health. Design strategies and architectures overlook
to adjacent neighborhoods, as well as personal
entropy, often operating under the contrived notion
Furthermore, this definition and discussion of health
interactions with site.
of static outcomes and complete control of systems.
lead to further critiques of current remediation
As described in AXIOM, DIG STUDIO problematized
THE METHOD
(how can I not get sued?), dramatic conditions and
resulted in the following:
adjacent terms, such as toxic or post-industrial,
models that rely on quick “fixes” and the landfilling
that referenced irregular and uncertain conditions
The grounding investigations and questions at the
In contrast, DIG STUDIO asserts that it is
within the contemporary landscape. The term
core of this project sought to understand the health
advantageous to engage entropy as a systemic
industrially-modified site is used to describe
implications of design as well challenge traditional
approach
those {sites} characterized by instances of “other”
design frameworks by addressing site complexity via
understand that designs can be insufficient, that
where
the embrace of entropy.
they can falter, or even fail; we are designing for that
conventional
ecological
disturbances
have been coupled with industrial disturbances, producing
new
ecologies,
to
nurturing
healthier
spaces.
of contaminated soil.
We
Current Remediation Models
potential failure. These insufficiencies and failures
Traditional or conventional “remediation” methods,
indeterminate
Moreover, initial research problemetized the mere
are opportunities for ecological and social health.
such as excavation via removal of millions of tons of
boundaries and unreferenced geographies, often
use of the word “health.” Health is especially
Before
process,
soil, capping and air sparging) are extremely invasive,
resulting in noxious, insalubrious economic and
difficult to define in industrially-modified sites due
Leann Andrews urged DIG STUDIO to create a
costly and often are ineffective— toxins are often
social epidemics.
to community perceptions, regulatory requirements
formal definition of health in context of this new
relocated to politically and economically poorer
02
launching
into
the
design
03
Asarco Smelter, Tacoma, WA, 2011. The site has been heavily excavated, leaving little trace of the former industry once vital to the waterfront. The construction of condominiums can be seen far lett.
The How: Entropy As Design Tactic
Self Organizing Systems [Stigmergy]
neighborhoods, “contained” (i.e. contaminants
popular in that brownfields are “remediated”
are dumped into a landfill or left within the soil
and “rehabilitated” as parks via experimental
under a clay cap). (NOTE: For a more in depth
bioremediation techniques (see precedents section
Entropy as design tactic is not just an exploration,
discussion of
current remediation practices,
of Haag’s Gas Works Park or Latz’s Duisburg-
but rather a critical & philosophical stance: a
Stigmergy is thought by many to be the principal
reference PHYTO PRIMER and/ or McCORMICK &
Nord). In this model, a site’s contaminated soil
way to move toward healthier spaces. In utilizing
mechanism
BAXTER).
may not be trucked to a landfill, the design
entropy as a an essential and core design tactic,
structures can arise “from the bottom up”, that is,
instead often utilizes an eighteen inch clay cap.
DIG STUDIO acknowledges what we don’t know,
through self-organized behavior of multitudinous
Current policies embraced by the EPA and
DIG STUDIO posits that industry or productive
while
traditional
agents that themselves have no conception of what
associated
enforce
place is vital to economic health. Furthermore,
conventions of shaping space as a basis for
they are building. As such, stigmergy is one of the
expediated timeline regulations for the remediation
these models promote ecological amnesia in
design. We engage concepts of duration, what
foundation stones for an atomist philosophy of
that the most users are ignorant of the active
DIG STUDIO views as “past scripts scores,”
biology: all the complex and wonderful contrivances
processes and slow seep of toxins in the ground
acknowledging that there are no static moments.
of the living world are explainable by the low-level
governmental
regulators
of contaminated sites (generally three years) that for
create
impossible
non-traditional
remediation
efforts
and
new such
barriers technological as
processes
and
remediation
efforts
to,
literally, take root. For further information on phytoremediation PRIMER.
research,
Particular
reference
conventional
following:
PHYTO methods
emphasize “Cut. Cover, Hide,” (such as at the Tacoma Asarco Smelter Site, page 03) which is
challenging
that is taking place underfoot. DIG STUDIO’s work
phyto/
bioremediation that require at least four years for
a typical remediation recipe that relies on the
simultaneously
1. “Removal” of toxins 2. Cap the remainder 3. Bake for several decades 4. Build condos 5. Address failed cap and infrastructure 6. Mitigate health impacts A newer, more experimental model has become
04
[Above] Gasworks, Seattle, WA [date unknown]. The activated burners were photographed by Landscape Architect Richard Haag before the site was stripped of most of its infrastructure. [Left] Gasworks reactivated and recalibrated as “Park”. Kite Hill contains the worst of the site’s contaminated soil.
whereby
complex
and
coherent
interaction of “atoms”, autonomous and indivisible
seeks to push the boundaries of Haag’s work
Entropy is employed as a means to chart
units that interact according to a discernible and
by promoting social, ecological and industrial
indeterminate
limited set of rules.
overlap through a combination of remediation
Transitioning industries and infrastructures have
tactics, technologies and programming.
the potential to generate & organize ecological &
and
contaminated
spaces.
social variety through the recruitment of, among other
processes, entropy. Entropy is a self-
organizing system.
05
—Scott Turner, Syracuse University
A sandbox is filled half with black sand and half with white sand. A little boy starts running in the sandbox. As he runs he kicks up and mixes the sand. When told to reverse his direction this does nothing to undo the actions of entropy driving the system towards uniformity. Robert Smithson’s definition of entropy in “Monuments of Passaic”
Header
Intersections
Sub-header
Artists have explored entropy as a means to explain and experience the world for much of the last century. In the early 20th Century, artists such as Kurt Schwitters, Marcel Duchamp, and Jean Arp in the 1920’s directly used entropy and methods of randomness within their projects. More recently artists such as John Cage and Robert Smithson have challenged and pushed ideas of what entropy might reveal about our world and ourselves. DIG STUDIO investigated particular artists whose work intersected with our own (i.e. John Cage, Ed Ruscha, Gordon Matta-Clark, and Robert Smithson to name just a few. For a more in depth discussion of artists, graph theory and music theory, please reference LITERATURE). John Cage was a composer
John Cage Music of Changes, 1951
Ruscha, Parking Lot #9, 1967
Clark, Splitting 1974
Smithson “Partially Buried Woodshed,” 1970
in the middle of the last century. He used chance operations as a method to exploit entropy as a means to distance the artist from egocentrism
06
07
as well as create a frame for outcomes that were
Gordon
uncontrolled by the artist. “Music of Changes” was
Matta-Clark
and
Robert
Smithson
ecologist and resilience-thinking
two types of system behavior: One can be termed
investigated the inherent failure of architecture over
pioneer C.S. Holling (1973) played an integral
stability that represents the ability of a system to
one of Cage’s first pieces in which he composed
time by showing its ephemerality. In Matta-Clark’s
role in our design and general understanding of
return to an equilibrium state after a temporary
the whole work using the I-Ching to determine
piece “Splitting,” a house slated for demolition
entropy. As discussed in LITERATURE, Holling
disturbance; the more rapidly it returns and the
the composition. Through the use of the I-Ching,
is split in two. Through this splitting, Matta-Clark
referred to the differing states of landscapes
less it fluctuates, the more stable it would be. But
Cage formed a musical composition via controlled
emphasizes the temporality of the building itself.
as “domains” (p10). These examples include
there is another property termed resilience that
randomness.
To Matta-Clark all architecture is a failure. Rather
historical and contemporary fisheries in the Great
is a measure of the persistence of systems and
than attempt to undermine this fact he chose to
Lakes, perch populations in Lake Windermere, and
of their ability to absorb change and disturbance
frame it in his art by emphasizing a structures end.
vegetation structure in grassland grazing areas of
and still maintain the same relationships between
the American West. Holling uses these cases to
populations or state variables (p14).
Ed Ruscha viewed entropy in the world all around
the work of
us, but especially in the urban landscape. Through his work, Ruscha attempted to capture the nature
Similarly, Smithson’s work reveals that everything
identify distinct domains of attraction in closed
of urban spaces that fall apart without intense
decays in time. In “Partially Buried Woodshed,” dirt
ecological systems. By qualifying their states as
DIG STUDIO also looked at the work of Chris Reed’s
maintenance regimes to keep everything in place.
was poured over a small structure until the roof
“domains,” (ibid), Holling is careful to state that
StossLU and his use of scaffolds within the design
In his series of aerial photographs of parking lots
caved in and the building collapsed. Smithson’s
these theoretically determinable models differ
process and how these might be used to generate
in Los Angeles, Ruscha captured not only the decay
piece sought to frame the limits within architecture,
from actual systems, where indeterminacy is more
form. StossLU’s Somerville Eco-Lab Demonstration
of these spaces, but also the necessity of these
with respect to both the physical structural system
prevalent, and a comprehensive analysis is often
Project is a prime example of how an initial scaffold
regimes. In “Lot #9,” the parking lots are clearly
as well as the systems that sustain it.
limited by data availability.
(a series of slopes and hills) combined with entropy
a collection of intense oil spots. Patterns of usage
(natural conditions such as rain and wind) could
and decay are made visible as well as their possible
In addition, theoretical landscape ecology models
Holling summarizes that concentrating on the
be used to spread seeds and examine bloom
future within abandoned businesses.
and design precedents from the past decade
“boundaries to the domain of attraction rather
cycles. The project is essentially a field test and
than on equilibrium states” allows one to identify
research study of successional and adaptive design
played a major role in our research. In particular,
08
(Above) Holling, 1970. (Below) rs.resalliance.org
09
The dream of architecture is to escape entropy... Entropy is the repressed condition of architecture.
strategies on an underutilized urban hillside. Stoss’s
+ 1,000 pathways + destination and dispersal +
Competition (New York, New York) presented
primary goal was to “test and seed a self-sustaining
sacrifice and safe = low-density metropolitan life.”
new forms of graphical representation that were
landscape using available stormwater and an
The proposal was an abstract diagram, similar to
either extremely spatial or struggled with temporal
understanding of inherent plant mechanisms (seed
Georges Seurat’s paintings, based on the circular
implications of dynamic landscapes. The premise
dispersal, dormancy, etc.)... Plants will colonize the
canopy of a tree and was extremely graphic due in
of
site and, potentially, nearby lots over a number of
large part to a partnership with Bruce Mao Studio.
graphics and models by various artists, composers
years, thus instigating an ecological transformation
Robert Smithson
in the city” (Lee 59).
StoSS LU, Eco-Lab, Somerville, MA. Tschumi notations.
DIG
STUDIO’s
examination
of
drawings,
and architects such as Karlheinz Stockhausen, The proposal, instead of prescribing a set of fixed
George Crumb, Anuradha Mathur/Dilip da Cunha
elements used in traditional masterplans, set out
and Bernard Tschumi (to name just a few) was to
DIG STUDIO is also a response to frameworks that
a range of opportunities that would evolve and
define and approach a communication style that
primarily began to emerge in competitions such as
shift over time. Ultimately, translating the abstract
was simultaneously spatial and temporal.
Freshkills and Downsview. DIG STUDIO used the five
diagram into a tangible space and successful urban
finalist entries from the Downsview Competition to
park proved too great a challenge. Mao dropped out
DIG STUDIO examined work by Architect Bernard
illuminate and prime reviewers as to what we were
of the project and the final constructed design fell
Tschumi’s Manhattan Transcipts and his Parc de la
trying to accomplish and avoid. The five finalist
back into static, well-tread masterplan techniques.
Villette Competition entry, perhaps most drawn to
entries for Downsview had much in common in
DIG STUDIO’s project is thus a challenge to and a
his grid of red follies (see barge follies McCORMICK
that they presented a configuration of frameworks
critique of the masterplan process.
& BAXTER), which are prominent in the Parc de la
that shape the park, but generate and recalibrate
Villette scheme. These works and notations begin
for growth over time. OMA’s winning proposal, TREE CITY, is more a formula than a design: “grow the park + manufacture nature + curate culture
10
Tschumi, Manhattan Transcripts.
Three of the five Downsview Competition Finalists ([OMA, Field Ops, Tschumi, FOA, B+SA ]
Moreover, representation in the famous Parc de
to describe sets of divergent occurrences and
la Villette (Paris, France) Competition, Downsview
cinematic mutations of space (physical and aural)
Competition (Toronto, Canada) and the Freshkills
with time signatures.
Stockhausen, Elektronische StudieIl.
11
Precedent Gas Works Park
site—that on-going remediation and public use
has left certain totems trapped behind a fence.
can and should be employed simultaniously, opened the public and the landscape profession’s
Rich Haag’s vision for Seattle’s gas works as a
Haag’s revolutionary—and thus cotroversial—
eyes to new ways of engaging the landscape via
new type of public park, offered an alternative
stance in addressing the challenges of a toxic
practice and design.
reading of a toxic post-industrial landscape in the city.
Gas Works Park (1972 masterplan,
1978 completion) is one of the earliest toxic industrial
sites to be remediated in order
to become a public space. Perhaps most importantly, it was the first public space to demonstrate nascent experimental techniques of phytoremediation and bio-remediation in the
FLUID TOPOGRAPHIES
early 1960s and 1970s.
CLAY CAP ASH & CINDER SAND SILT & GRAVEL SAND SILT & GRAVEL
Gas Works Park is the last remaining survivor of
GLACIAL TILL
1906 CONFIGURATION
1400 gasification plants in the United States.
Richard Haag
members of an extinct species. The last decade
SEATTLE GAS LIGHT SERVICE RADIUS
New eyes for old... Permanent oil slicks became plains with outcroppings of concrete, industrial middens were drumlins, the towers were ferro-forests and their brooding presence became the most sacred of symbols.
BIOREMEDIATION 101
TAR WELL
= =
Much of the plant’s infrastructure was removed
enzyme PAHs
(images, right); however, the remaining relics (such as the burners of the former Gas Plant serve as totemic artifacts; the last surviving
12
(Top to Bottom) botanical, fragment, context.
Gas Works Park, Thick Section (temporal and spatial qualities collide to convey historical, industrial, ecological and social qualities of site. Rendering by Tera Hatfield.
13
For an industrial ruin to maintain that history while constructing new use and meaning — this is what I call the sublime.” Julie Bargmann, Terragram Dispatch Nº1
Precedent Vintondale Reclamation Park
Stacy Levy, artist; T. Allan Comp, historian and director of non-profit AMD & ART; Robert Deason, work of transforming 40 acres of former coal mine whose grounds and on-site water were thoroughly
mining pollutant as an opportunity to transform
finishing in 2000. The final site intermingles wetland
makes the important statement that “Environmental
an industrial wasteland into an abundant
ecology, industrial mine artifacts, spaces of leisure and
problems are created and defined not by science, but
landscape, a renewed place.
didactic treatments systems that create new forms and
by our culture.” Comp states that, in effect, they are
In 1995, Julie Bargmann and collaborators (including
hydrogeologist; and AmeriCorp Interns) began the
“Designing the Reclaimed Landscape,” T. Alan Comp
The entire process is depicted in a series of six etched metal panels, from site history and context to design interventions and treatment.
contaminated with acid mine drainage (AMD) (DIRT
2008). Local ecosystems and watersheds are
Studio 2010). Collaborator Alan T. Comp cites the
devastated due to coated stream beds that effectively
community engagement efforts as a crucial component
kill all organisms by raising the acidity levels of the
for the success of the project (Comp 2008).
water to an intolerable degree (AMD & ART 2010). Since the coal and steel mines of the area were
cultural artifacts, and effective remediation depends
TESTING
on one’s ability to address the problems “with the
combining expertise in science, history, art, and
full range of the arts and humanities, as well as the
design toward the synthetic creation of a complex
sciences” (Comp 2008, 63).
landscape. Working with residents and citizen
The Vintondale Reclamation Park is perhaps a
groups, local governments, state and federal
prototypical case study because the design clearly
In a special issue of Landscape Architecture on Eco-
agencies as a model for other communities to
uses the on-site layers of accumulated toxicity, history,
Revelatory Design, Julie Bargmann and Stacy Levy
initiate the reclamation process.
and meaning in a dynamic manner that works to
the
interdisciplinary
process
of
don’t so much write a review of their work at Vintondale
a series of six etched metal panels, from site history and context to design interventions and treatment.
simultaneously hold complexity and conflict in view
as issue a set of rules and criteria used to reclaim the
TESTING the acidic mine discharges and using
while presenting a new notion of beauty that is ever
site. Bargmann and Levy stress Comp’s important
industrial-strength, bioengineered systems to
changing and supportive of public engagement. The
points about community and reclamation under the
cleanse the water. Inviting the public to witness
collaborators seem to have succeeded in giving legible
modus of “TESTING”:
this treatment process, offering an understanding
form to ecological and industrial processes, mixing
of how they can actively participate in the
these with spaces for play, recreation and delight that
regeneration of
are accepted and embraced by the community. Perhaps
The tell tale rust colored streams tainted with AMD
closed after WWII, the local community of Vintondale
are abundant in the Appalachian coal country. AMD
has dealt with significant poverty and decreases in
is created by a chemical reaction when rainwater and
population due to lack of employment. In addition
TESTING the endeavor to reclaim an industrial
groundwater mingle “with abandoned mine workings”
to these social issues, the environmental problems
landscape
(Bargmann 1998, 39). The reaction results in an
spurred by the area’s mining history have persisted
a
acidic, metal concoction that seeps into neighboring
and accumulated over time to rob citizens of potable
community. Seizing the crisis caused by a post-
water sources, coating them in oxified iron (Comp
water and valuable recreational opportunities. In
14
definitions of beauty. The entire process is depicted in
as
a
contaminated
regenerative ecology
and
catalyst a
for
declining
their landscape and their
what is missing is a formal engagement with not only
community.
the ecological and social health of the community, but The design was completed in 1998 with construction
15
also an economic engagement in its recovery as well.
Nature depends on technology; technology depends on nature. The park’s entire water system is a planned ecology.
Precedent Duisburg-Nord Landschaftspark Duisburg-Nord
Landschaftspark
is
a
post-
industrial reclamation project on 180 hectares, located outside Dusseldorf in the industrial belt of the Rurh Valley, in Northern Germany. Latz and Partners began the design work around 1990, after residents prevented the razing of the steel mill after it shut down in 1985. As the facility had
Peter Latz
been abandoned for sometime before any plans could be implemented, nature had already began taking back the park. preservation
Latz’s design combines
architecture,
reclamation,
and
incidental phytoremediation alongside assorted
remediated (such as the stripping of accessible
Documenting such an enormous site is quite
electrical fixtures) or cordoned off; the existing
challenging, but after reviewing both sketches and
successional growth was documented and allowed
photos, several categories emerge: botanicals;
to proceed; architectural features were adapted
context; fragments; passages; and relics; each
to new uses, which included renovation and
having their own sense of scale and framing–both
demolition; demolition of selected architectural
temporal and spatial. The botanical category
constructs permitted their foundations to join
focuses on some of the minute details of singular
the landscape matrix; procession through the
vegetative growth within the park. Context depicts
industrial relics was choreographed to permit
the surrounding area. Fragments present portions
access to certain objects; new walkways were
of the park that convey the gestalt of the whole.
combined with existing circulation to create a
Passages address the syntax of circulation, both
woven route through the site; selected cells within
new and adapted.
the foundry were planted in the style of a classical
large industrial assemblage that constitutes
landscape in rhetorical configurations; and many
the core identity of the park, its history, and its
objects were modified or repurposed for new
iconography.
And relics documents the
programs, such as a garden, a climbing gym, or
landscape tropes. The park permits a new mode
a slide that echoes the extensive steel duct work
of inhabitation of a once brutal landscape and
that characterizes the site.
infrastructure.
Likewise, existing
growth was augmented with additional plantings, such as betula pendula and other plants that
Latz’s design included many low-impact design strategies: hazardous conditions were either
16
(Top to Bottom) botanical, fragment, context.
colonize disturbed sites.
Varied passages.
17
HOTSPOT: GAME BEGINS HERE
archive {set a1} offers a set of initial instructions
intrinsic entropic forces within the design
and processes for the Willamette River’s industrial
process and ecological interventions. Scripts
edge. Many of our initial scripts were written for
(or sets of scripts called scores) are a sequence
biological and phytoremediation of contaminated
of instructions that can be interpreted and
soils, and groundwater; however, as the writing
carried out. This definition originates from the
process evolved, biological and technological
etymology of script as simply “the dialogue
agents
and
and instructions for a play, musical or other
temporal forms that work with the various edge
performance work” as well as “to scratch an
conditions (fallow, transitional, industrial).
outline, sketch, from base ‘sker-’ cut, incise.”
THE METHOD
Here, we divorce scripting from modern usage
1. Overlay the gameboard (hexagonal tesselation)
and
2. Examine script archive/ in process scripts & scores
and parametric modeling programs such as
3. Write scripts
Grasshopper, Maya and Python, that employ
commingle
to
create
scaffolds
> individual scripts are initially written based
Downtown Portland
associations
with
digital
computation
iterative computational geometry to “generate”
on chemical plumes present in the river,
formal, finite architectural designs. This latter
in sediment/soil, & in groundwater (hotpots)
computational
C
+
C
C H
H
C
C C
=
p
H
H
IMPAIRMENT [E.G BENEZENE]
R E M E DI A T OR
RESULTANT
scripts by-product of in-process scripts > initial program and performance [RECIPE FOR EXPERIENCE] TECHNOLOGY A.
1. O I L
4. Run script(s)
employed by Cecil Balmond and Jenny Sabin at
3. B-TEX
> programming and spatial form arise from
University of Pennsylvania’s Nonlinear Systems Organization research group.
is
H
2. PAHs
18
strategy
[INITIAL PERFORMANCE]
H
heavily
scripting tactics when compounded along a time axis
design
GENERAL SCRIPT
TECHNOLOGY B.
4. PHTHALATES
19
+
+
USER INTERFACE
BRACE [THE GAMEBOARD]
Scripts are a design tactic utilized to embrace
RAIL CONSTANT
TACTICS
INDUSTRIAL PORT OF PORTLAND : //
The Method
As introduced in the SCRIPT SET, the script
=
While we find these alternative and experimental digital
strategies
interesting,
DIG
STUDIO’s
investigation and embrace of entropy seeks to challenge the notion of the static masterplan. Parametric modeling, despite its complex and often
chemical components of both living organisms
scripts
and harmful chemicals. In this sense, hexagons
by-product of in-process scripts > performance> charting indeterminacy VARIABLE SITE RESULTANTS
watershed scale. In addition, DIG STUDIO chose the hexagon as a rhetorical device because it
curved results, is merely another strategy focused
VARIABLE SITE RESULTANTS
work as a perfect scalar on a molecular, plume or
H H
reveals the arbitrary and static boundaries, both H
that results in a static structure or landscape. In contrast, scripts are designed processes (both engineered and “natural”) that are inserted into and onto specific site surfaces, geology and ecology. As a result, scripts have often unpredictable by-products,
economic and political, that are used to govern
H
C C
C C
fluctuating and dynamic systems within our urban
+
C
C H
H
T R A JECT O R Y
H
landscapes. Hexagons are a wink and a nudge. As
H
+
C
C
on an end product that fails to adapt and change,
H
C C
C C
RAIL
H
H
ORGINAL REMEDIATION SCRIPT
Elizabeth Meyer states, “Toxicity flows,” it knows
H
no boundaries.
ORIGINAL REMEDIATION SCRIPT
which is how we are seeking to chart indeterminacy.
IVE
AT
(six sided, composed of triangles) that make it
G HIN NC BR A
CH E
OR
What the Hex?
C
reasons. Hexagons have mathematical properties
MI
mutations. In addition, scripts engage critical user
AB
signifying a hotspot or insertion point for various LL CO
indeterminacies while allowing for adaptations and
SWARM
CA L
with a hexagonal gameboard with one hexagon
MI
landscape. Scripts are in a continual state of flux.
WS
O FL
the point of insertion. Scripts narrow the range of
IZO
a conscious choice. DIG STUDIO chose to work
RH
basis in turn shapes process scripts such as the
AGGREGATE
uniquely suited as a building block. Moreover,
users, creating engaged, healthy spaces. How users
hexagons are also found in nature as base structural CK
IN
G
The repetition of hexagons within this work is
PA
interact and experience these processes on a daily
PRESENT INSERTED SCRIPT
POSSIBLE FUTURES
POSSIBLE FUTURES
TEMPORAL ANALOG OF THE FUTURE [UNBRACKETED] 360° POSSIBILITIES
TEMPORAL ANALOG OF THE FUTURE [BRACKETED] CONAL POSSIBILITIES
WHAT THE HEX?
Scripts result in directed trajectories, marked from
interface issues. Scripts interact and perform for
PRESENT NO SCRIPT
20
21
SCRIPTING BASICS & OPEN SOURCE
SCRIPT ARCHIVE
01
THE ARCHIVE
INTRODUCTION
SCRIPT ARCHIVE
Basics
As introduced in the methodology section of Scripting
digital
101, scripts are a design tactic utilized to embrace
investigation and embrace of entropy seeks to
intrinsic entropic forces within the design process
challenge the notion of the static masterplan.
and ecologies. Scripts are a sequence of instructions
Parametric modeling, despite its complex and often
that can be interpreted and carried out.This definition
curved results, is merely another strategy focused
originates from the etymology of script as simply
on an end product that fails to adapt and change,
“the dialogue and instructions for a play, musical or
that results in a static structure or landscape. In
other performance work” as well as “to scratch an
contrast, scripts are designed processes (both
outline, sketch, from base ‘sker-’ cut, incise.”
engineered and “natural”) that are inserted into and
strategies
interesting,
DIG
STUDIO’s
onto specific site surfaces, geology and ecology. As a Here, we divorce scripting from modern usage and
result, scripts have often unpredictable by-products,
associations with digital computation and parametric
which is how we are seeking to chart indeterminacy.
modeling programs such as Grasshopper, Maya
Scripts result in directed trajectories, marked from
and Python, which employ iterative computational
the point of insertion. Scripts narrow the range of
geometry to “generate” fomal, finite architectural
indeterminacies while allowing for adaptations and
designs. This computational design strategy is
mutations. In addition, scripts engage critical user
heavly employed by Cecil Balmond and Jenny Sabin
interface issues. Scripts interact and perform for
at University of Pennsylvania’s Nonlinear Systems
users, creating engaged, healthy spaces. How users
Organization research group.
interact and experience these processes on a daily basis in turn shapes in process scripts. Scripts are in
While we find these alternative and experimental
02
a continual state of flux.
03
The script archive {set a1} offers a set of initial instructions and processes for the Willamette River’s Industrial edge. Many of our initial scripts
as the writing process evolved, with biological and technological agents comingling, scaffolds and temporal forms were created that work with the various edge conditions (fallow, transitional, industrial). The following pages will provide short descriptions of initial scripts we wrote
SCRIPTS
A CLOSER EXAMINATION
over the course of a few weeks while analyzing the industrial Port of Portland. These scripts were written and geocoded for specific inserstion
RAIL CONSTANT
of contaminated soils, groundwater; however,
USER INTERFACE
were written for biological and phyto remediation
points and surface locations, illustrated in the geocoded gambeboard map fold-out (last page). Scripts offer a way forward to maximize landuse efficiency, comingling industry as well as ecological and social services.
Scripts were developed with the intention of maximizing the interface between site and user. Multiple layers of interface functionality is built into the site via scripts.
04
Against the change inherent in designing with the indeterminate nature of these scripts a constant helps to root the design and create a foil against which processes can be seen. The rail has a historical presence in the port and plays an important role in its future; therefore, it makes sense as a constant to be incorporated in various forms across the site.
climate change
Pb
+
Pb
=
Pb Pb
Pb Pb
5 4 3
SEA LEVEL RISE
Sea level rise is a known future. How can its indeterminate effects be incorporated into a site design.
Lead is a heavy metal found on many of the sites throughout the port. Certain plants can function as hyperaccumulators for this metal
05
SEQUESTRATION
Pb
Pb
&
+
= BANKRESTORATION
In a traditional manner, heavy equipment and a heavy hand are used to transform the steep slopes of the shoreline into a functional form that better aligns itself with shoreline and river stage processes.
06
H
H
C
C
H
C
C
C
C
C
C
C
H
C
H
+
=
H
NAPHTHALENE
Endophitically enhanced grasses can be planted in areas with high PAH’s in the soil. The endophites allow plants to use the carbon in the compound for growth while breaking down the PAH into its constiuent parts.
07
H H
H
C C
C H
C C C
H
C C C C
H H
H
,
ROBUST GRASSES
H
H
BROKEN PHA’S
(POLYAROMATIC HYDROCARBONS)
PAH’s
EG.
MERCURY
+
= JUNCUS MARITIMUS
FRESHMARSH
Heavy metals, especially mercury, build up in water and ocean conditions. Certain plants such as Juncus maritimus have been found to fold and sequester those metals in their cell structures. Through the insertion of these plants, heavy metals can be collected and reused.
08
SEQUESTRATION
Hg
+
SEQUESTRATION
As
=
CHINESE BRAKE
FERN Chinese brake fern is another example of a plant that has been found to sequester Arsenic in its leaves, allowing for the collection and safe removal of toxic metals.
The Lower Willamette River provides major habitat connectivity between the Columbia River and the upper Willamette Valley, including the further stream reaches of the Cascade and Coastal Ranges. Maintenance of existing --and provision of new--habitats in indicated by this script.
09
CADMIUM
+
= NICOTIANA
TABACUM
Tabacco is another hyperaccumulator that is especially efficient in the collection and sequestration of cadmium.
10
Cd Cd Cd
Cd Cd
SEQUESTRATION
Cd
Cd
HEAVYMETAL GMO ORGANICCHEMICAL POPLARS Poplars are one of the best plants for phytoremediation techniques. They readily adapt to new endophytic bacteria and spread their roots very deeply to allow for cleaning hard to reach water tables. They may also be genetically modified to enhance their cleansing functionality and work as a hyperaccumulator for heavy metals.
11
TCE
TCE
BIODEGRADATION
ACCUMULATION
=
+
TCE
TCE
HEAVYMETAL ORGANICCHEMICAL
PAH
H C
BTEX PAH
Cd
Floating remediation islands comprised of phytoremediatory plants can be starter seeds for near shore cleaning. Constructed of durable, non-toxic post-consumer plastics and vegetated with with a mix of plants, these islands function on multiple levels (habitat and remediation and be tailored for specific locations. After the rootbag disintigrates, the islands, equiped with sensory technology, are free to move to any location or drift with the currents for further remediation down river.
12
H
Cd
Cd
REMISLAND
& Cl
C
Cl
BIODEGRADATION OGRANICCHEMS
+
BIND+SEQUESTER
=
BTEX
BTEX
PAH
+
=
Cd
BTEX PAH
Cd Cd
The remediation island typology is adapted to an extensive green roof / lid structure. Alternate configurations replace botanical hex modules with skylights, solar panels or other architecturally explicit functions. The surface of the completed lid serves as a park, extending from the Waud cliffs (or other location) and meeting the river bank. Alternate lid topographies can be accommodated.
13
CONTAMINATED
+
GROUNDWATER
= NANOTUBE
Nanotechnology has lead to the creation of tiny cleaning particles. Through the placement of tubes that pierce contaminated groundwater wells, nano cleansers within the tube can filter and clean water. This creates a visual of the cleaning process legible to visitors.
14
CLEANSED WATER
+
FILTER+DEGRADE
+ + + + +++ + +
= NANOBUCK
Another example of nanotechnology at work. Tiny nanopaticles collect contaminantes in river sediment and latch them together. These particles can build up and be removed or rendered inert.
15
TCE
TCE
PAH
PAH
CLEANSED RIVER SEDIMENT
CONTAMINATED RIVERSEDIMENT
ACCUMULATOR
+
TCE
The port itself, and its economic function, is another possible insertion into a site. To allow for greater economic, social and ecological functions, it may be necessary to recalibrate landuse patterns in and around the port system to provide for multi-functional landscapes.
16
WASTEWATER
EFFLUENT
= WILLOW
BIRCH
Wetland plants, such as willows and birches, can function to clean wastewaters and effluents from nearby neighborhoods. The plants could then be used as a source of biofuel for energy production in small scale local powerplants. 17
EFFLUENT TREATMENT BIOFUEL PRODUCTION STORMWATER DETENTION
+
+ TOLUENE
= ENDOPHTYE++
POPLAR
Endophytically enhanced poplars are be used to remove and remediate organic materials such as BTEX. When the roots are of a mature age (i.e. grown deep), contaminated groundwater plumes are effectively stopped by the endophytes.
18
&
H H C
H
BREAK DOWN OF BTEX COMPOUNDS
EG.
CH3
PLUME STOPPAGE AFTER ROOT GROWTH
BTEX
TNT
N
N
&
N
O2N
NO2
=
NO2
O2N
+
RD
NO2
TNT RD
RD
A further example of how endophytic bacteria remediates toxic chemicals that are often found together. TNT and RDX (two chemicals found together from explosive degredation).
19
X
GMO GRASS OUTCOMPETED
CH3
BROKEN RDX
NO2
SEQUESTER TNT
TNT
GEOCODED GAMEBOARD
REGIONAL SCRIPT
After Dig studio selected the Port of Portland as its final site the combing the data and compiling of information and the simple act of wrapping out heads around what we were looking at had to be done.
Regional Analysis Sifting and Churning
As an initial step in the investigatory process DIG studio sifted through many databases containing information related to the industrial port of Portland as a whole and zooming out further to encompass the broader Columbia basin. This data came in the form of GIS data, EPA data sheets, executive summaries, and a plethora of other information. From there various maps were created and compilations of information all
Sifting and Churning
Regional Analysis
with the goal of furthering our understanding.
02
03
GIS tracings As a way of cataloguing the information a series of small maps depicting the tracings of data were created. Each map shows a single piece of information derived from the GIS data that we were able to dig up. These maps are bracketed by the confluence of the Willamette and the Columbia river at the north, and the T.W. Sullivan Dam to the south, the first dam on the Willamette. From this effort we were able to build a better base of information on about the greater context of region. This information pointed to the broader context of systems and control in place. These systems have effects all the way down to the scale of the individual spaces along the Willamette.
Dams
Fires
04
05
COLUMBIA/ WILLIAMETTE CONFLUENCE
Power Grid T.W.SULLIVAN DAM
COLUMBIA/ WILLIAMETTE CONFLUENCE
Rails
COLUMBIA/ WILLIAMETTE CONFLUENCE
T.W.SULLIVAN DAM
06
Steep slopes
T.W.SULLIVAN DAM
07
Parks
COLUMBIA/ WILLIAMETTE CONFLUENCE
COLUMBIA/ WILLIAMETTE CONFLUENCE
T.W.SULLIVAN DAM
Deactivating
COLUMBIA/ WILLIAMETTE CONFLUENCE
T.W.SULLIVAN DAM
Wetland
COLUMBIA/ WILLIAMETTE CONFLUENCE
T.W.SULLIVAN DAM
08
Active
T.W.SULLIVAN DAM
09
96 flood
COLUMBIA/ WILLIAMETTE CONFLUENCE
COLUMBIA/ WILLIAMETTE CONFLUENCE
T.W.SULLIVAN DAM
Metro open canopy
COLUMBIA/ WILLIAMETTE CONFLUENCE
T.W.SULLIVAN DAM
Buildings
COLUMBIA/ WILLIAMETTE CONFLUENCE
T.W.SULLIVAN DAM
10
100y flood
T.W.SULLIVAN DAM
11
Canopy cover
COLUMBIA/ WILLIAMETTE CONFLUENCE
COLUMBIA/ WILLIAMETTE CONFLUENCE
T.W.SULLIVAN DAM
Vacant lots
COLUMBIA/ WILLIAMETTE CONFLUENCE
T.W.SULLIVAN DAM
10ft contours
COLUMBIA/ WILLIAMETTE CONFLUENCE
T.W.SULLIVAN DAM
12
UGB history
T.W.SULLIVAN DAM
13
DEM
Conceptual mapping After creating tracings of data at a larger scale certain areas and sites started to stand out as specifically interesting. Much of this interest came from the relationship of the sites to the broader processes that we were seeing such as chemical plumes. The geographic relationships that some of these sites had to the neighborhoods and industries created in triguing situations as well. Some of these sites were interesting due to the differences that were apparent between them, such as the openness phthalate PAH’s
of McCormick and Baxter vs. the tight industrial qualities of the railyard
Heavy Metals
or Schnitzer steel. Information about those sites then incorporated into conceptual maps showing flows and relationships inside and outside the site. From this exercise we were able to visualize the interlinking of the various systems
hydrocarbons/oil heavy metals
oils/hydrocarbons
on the site.
heavy metals pah’s phthalate
pah’s
oils/hydrocarbons heavy metals phthalate
hydrocarbons/oil
heavy metals pah’s
heavy metals
PAH’s
Conceptual index The flows up and down the industrial port and the inter-relationships of some key sites
14
15
A large fallow region central to the industrial port where there once were thriving industries. Many chemicals flow out from these sites now.
16 17
beneath the Premier Edible Oils portion of the site contains low levels of chlorinated solvents and petroleum constituents. A 1998 subsurface investigation at the Boydstun Metal Works portion of the site (ECSI #2362) revealed low levels of chlorinated solvents in groundwater, and soil contamination from metals, petroleum, and PCBs.
landfilled PCBs As,Be,Sb,Be Cu,Pb,Ni,Cr,Zn PAHs TPH possible PCP possible dioxins methylene chloride asbestos
GROUNDWATER
Antimony, arsenic, barium, beryllium, cadmium, chromium, cobalt, copper, iron, lead, manganese, mercury, nickel, zinc, 2-methylnaphthalene, organotins, PAHs, bis(2-ethylhexyl) phthalate, butylbenzylphthalate, carbazole, and dibenzofuran are present in sediments adjacent to the site, based on a 1997 sediment study conducted by EPA in the Portland Harbor section of the Willamette River. Contaminants that have been documented onsite include petroleum hydrocarbons and related constituents; chlorinated solvents; metals; and PCBs.
Sb drift
PAHs BTEX phenols 2,4-D voc pah pcb hydrocarbons
SEDIMENTS
As 2010
10 Fe2+
YEAR CYCLE
2006
Be
landfilled
Cd
Ba
Cr
n 1:3000
n 1:3000
Schnitzer steel to the north has had a number of shifting materials and uses over the years as well as a number of heavy metal seepages into the water table.
petroleum hydrocarbons benzene toluene ethylbenzene xylenes PAHs heavy metals
DDT
Petroleum compounds
diesel and oil
paint-related solvents and metals lead zinc bis(2-ethylhexyl)phthalate butylbenzylphthalate di-n-octylphthalate
n 1:3000
n 1:3000
The west side tank farm has a variety of chemical flows outward to the river
18
Albina rail yard has major rail flows going north and south of it. A history of fuel spills inside and outside contained areas cause infiltrations into the river.
19
Key Watersheds COLUMBIA RIVER BASIN
Scaling up from the water flowing past the key locations in the port there are several watersheds that the river is nested in
WILLAMETTE RIVER BASIN
Columbia River Basin:
The Columbia River Basin drains over 260,000 square miles
of Washington, Oregon, Idaho, Montana, and British Columbia. It is over 1,200 miles long with major tributaries ranging into the tens of thousands of miles and minor tributaries in the hundreds of thousands (River Keeper 2012). There are over 450 dams within the basin that shape historical salmon runs, numbering close to 16 million salmon and steelhead (ibid). These dams produce 50% of the region’s electricity, promoting current and future conflicts between hydropower and the endangered species act. Simultaneous conflicts arise within the basin between irrigation requirements for agriculture and flow regimes for spawning salmon.
Lower Willamette River: “The Willamette River is the 13th largest river in the contiguous United
01
LOWER WILLAMETTE HUC6 1 &2
A B C 02
HUC6-2
Flows vary considerably by season, with the lowest flows occurring during the late-summer dry season, typically increasing by 10 times through the winter rainy season. River flows in the LWR are regulated to some degree by a series of upstream dams, although major floods of 200,000 cubic feet per second or more still occur every few years during large storms. Despite periodic scouring of some locations by floods, the Study Area is situated in a relatively low energy, depositional
D1
reach of the LWR. Although the LWR is over 100 miles from the Pacific
D2
Ocean, it is influenced by tides. Tides cause the river stage to rise and
E G
HUC6-1
States, with substantial flows, averaging 33,000 cubic feet per second.
F H J
fall up to several feet through a tidal cycle. During the dry season, when river discharge is low, rising tides can cause intermittent flow reversals throughout the harbor.” (LWG 2011 pES-5).
HUC6-1&2: HUC6-1: 1,621,762,453= 37,230 acres = 58.2 sqmi HUC6-2: 1,806,861,986 = 41,480 acres = 64.8 sqmi
PORTLAND INDUSTRIAL PORT
20
21
Within the Port a few key locations stood out that helped to sumarize the function of the port itself and show the many different land uses and relationships.
Confluence The meeting point of the Willamette and the Columbia river. The extents
01 CONFLUENCE
of the industrial port.
Toyota Lot Location for unloading large shipments of imported cars that are then loaded onto trains and trucks for shipment inland.
C TOYOTA LOTS
McCormick and Baxter Now a fallow and defunct industrial space. It had been the location of a number of different industries over the last century including ship building and chemical storage
D2 McCORMIC & BAXTER
BNSF Albina Railyard Extensive railyard that lies just south of Swan Island. Serving as a major rail depot for the port.
F ALBINA RAILYARDS
22
23
Schnitzer Steel A major large scale metals recycling and manufacturing company. The site consists of many large stockpiles of steel waiting to be recycled and reworked.
A SCHNITZER
Cathedral Park A large waterfront park located within the neighborhood central to the industrial port. This is one of the few existing locations for the general public to interact with the waterfront within the industrial district.
02 CATHEDRAL PARK
Arkema A former pesticide plant. The site is now contaminated with DDT and various breakdown products from the production of the pesticide.
D1 ARKEMA
Fremont Bridge The Southernmost extents of the industrial port. The Fremont bridge marks the beginning of the downtown on the west side and denser residential neighborhoods on the east side.
J FREEMONT BRIDGE
24
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LOCAL ANALYSIS
Local Analysis
With a focus on the industrial port of Portland DIG STUDIO analysed the port as a whole for influences on the dynamic landscape. Along
Industrial Information
with mapping these influences, DIG STUDIO speculated about the future of the spaces and how they might develop.
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Topo
These sections illuminate the relationship within the river basin, from the hills and Forest Park in the west to the Skidmore bluffs in the east
TRANSECT 5
Topography of the Willamette
that both separate the infilled flood plane. This flood plane is now
1:12500
occupied by industry, from the residential neighborhoods above them.
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05
Hard
The extents of the orange color on this map represent the areas of impervious surfaces throughout the industrial port of Portland. This
Impervious Surfaces
map clearly illustrates the extent of industrial areas, which are in close proximity to the river. These industrial areas have the greatest amount of impervious surface. Extending up the west hills, Forest Park has little to no imperviousness. The residential neighborhoods above the Skidmore Bluffs are a mix impervious/pervious surfaces,
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HARD
typical of most residential areas.
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07
Vegetation
The red areas of this map represent areas of pervious surfaces, such as lawns, grass or unvegetated soils. The orange represents areas of
Pervious/Forested surfaces
canopy cover. Parks, hill sides, street trees, and parks all fall under this category. Again, the stark difference between the impervious infilled flood plane and the surrounding areas can be seen in the void
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VEGETATION
spaces along the shoreline.
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09
BEACH
Edge
Descriptions of the shoreline condition through the industrial port are represented through various typologies.
Shoreline Conditions
TYPOLOGIES Bulkhead Defined by a hard vertical surface that separates the water completely from the land.
Sometimes this bulkhead extends considerable
distances above the water level to allow for barges and large vessels
BEACH
to dock beside them.
RIPRAP BEACH
Riprap BEACH
The aggregation of rocks along the shoreline protects the land from erosion by the forces inherent in the river. They also inhibit natural river processes and disturb river ecosystems by removing nearshore
RIPRAP BEACH RIPRAP
habitat.
CONDITIONS & TRANSISTIONAL RANGE* BEACH
BEACH
*distance b/w water and distinct land use component
BULKHEAD
RIPRAP RIPRAP RIPRAP BEACH
BULKHEAD
BEACH RIPRAP BEACH
The land meets the water at a gradual angle so that the water can be entered and near shore habitats may be feasibly established.
BEACH
BULKHEAD
Beach
Transitional Distance The shoreline conditions were placed within the context of the nearest shore usages (i.e. the general distance from the waterline to the nearest distinct land use). For example, this land use might be characterized as a building or a parking lot. 0 ft usually delineates a bulkhead condition. 0-100 ft often describes riprap and possibly beach conditions.
RIPRAP
100-500 ft distances can vary in shoreline—it
often reflects a now defunct land use, such as fallow fields. +500
RIPRAP
ft illustrates that the distance is great enough so that direct impact of the land use on the shoreline and water is not greatly noticeable.
BEACH BEACH RIPRAP BULKHEAD
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EDGE
RIPRAP
10
BULKHEAD
RIPRAP
11
RM-1
Edge Flex
This analysis provides a description of the amount of speculative change that DIG STUDIO foresees as possible at different point RM-2
locations along the waterfront.
HIGH
Shoreline future possibilities
Through the analysis of the land
uses along the waterfront and knowledge gathered about the future of existing land uses, DIG STUDIO created a rating for points along the waterfront to speculate how flexible (for change in use and
RM-3
SHORELINE FLUX & XXXX
industry) points along the waterfront may be. These values were
INDUSTRY
a visualization of the areas with the greatest flexibility within the
ECO-SERVICES Industy and ecosystem services co-exist, always overlapping to various degrees.
EAST BANK RM-1
water to land transition. The graph to the left shows a breakdown by river mile of the same graph that is shown overlayed on the map. From these visualizations, it is clear what areas of the river have the greatest potential for change and the rhythm they create moving
RM-2
RM-3
RM-4
RM-5
RM-6
RM-7
RM-8
WEST BANK
RM-4
graphed horizontally from the shoreline on the map in order to give
RM-9
RM-10
RM-11
RM-12
down the river.
Eco/Industrial Gradient Key areas along the shoreline have a bar that delineates
the
possible amount of overlap between future industrial usages and new ecological functions. The areas with the greatest amount of flexibility also have the greatest potential for ecological insertions. RM-5
RM-6
RM-7
n>
EDGE FLEX
RM-8
RM-9
RM-10
12
RM-11
13
Rail
The railroad historically played a significant role in the development of the industrial port of Portland. The areas surrounding the water
Railroad track extents
are still dominated by railroad tracks and railyards that carry goods both locally between industries as well as long distances. The port of Portland has long been a major west coast port for goods coming into the country before they transported inland. The map illustrates the rail tracks domination of the waterfront. Rail that does not need to be located by the waterfront (BNSF Albina yard) dominate major stretches of urban waterfront. These major features must be incorporated into the landscape or engaged in a
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RAIL
meaningful way.
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PATH TYPE H20 landing Existing terestrial Existing water PDX planned PDX conceptual
Connectivity
The shoreline physically connects upward via the Skidmore bluffs into the surrounding communities; however, it lacks existing
Bike/Ped paths & connections
pedestrian connections. The existing and future connections around the shoreline are depicted in this map. The city of Portland has a clear plan to create better connectivity along the shoreline in all parts of the city.
TYPOLOGIES Existing terrestrial These are the existing bike and pedestrian paths through the industrial port and surrounding areas
Existing Water This is all the navigable water routes including the main shipping channel in the river.
PDX Planned These are paths the City of Portland has planned and hopes to implement in the coming decade.
PDX Conceptual These connections are seen by the City of Portland as desired and feasible but there are currently no specific plans to create or implement these paths.
H2O Landings These are locations of small boat landings and boat ramps for
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CONNECTIVITY
recreational use.
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TRAILS 2.0 H20 landings Terestrial
Extensions
DIG STUDIO proposes further connectivity developments beyond those of the City of Portland. This map illustrates a possible layout
Further connections
of paths through the industrial port and where additional water
n>
EXTENSIONS
landings could exist.
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SUPERFUND TAX LOT No. SEE CHEMICAL INDEX
0
[De]Active
Remedial Investigation Summary
Contamination of active and deactive locations
2
The Superfund Site is located in the Lower Willamette River, between Sauvie Island at RM1.9, and Broadway Bridge at RM 11.8.
While
earlier clean-ups were conducted by the Oregon Department of Ecology 3
(DOE), the DOE ceded oversight to the EPA by early 2000. After EPA requirements are satisfied, properties are referred back to the DOE for further brownfield remediation.
4
The Portland Harbor Remedial Investigation (2001-2008) identified 65
89 contaminants that pose “unacceptable risk across all ecological
5 64
7
6
receptors, e.g. birds, fish, etc.,” (LWG 2011). Twenty-nine of these
8
63
9
61
chemicals were identified as posing a human health risk (ibid). These chemcials are distributed throughout sixty-five sites identified as
10
11
contributors to the larger Port of Portland Superfund Site. The main toxins of concern correspond to families of chemicals related to PCBs,
12
60
PAHs, DDx and dioxins and furans, but also include heavy metals. The report summarizes the extensive list categorically as: metals, tributyltin
13 59
14
ion, PCBs, dioxins, DDx and other pesticides, semivolatile and volatile organics, phenols, herbicides, and polybrominated diphenyl ethers
15
(PBDEs) (ibid). See DIG::\ Appendix-A for a complete list.
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55
Contaminants reach study areas through variable pathways, including:
16A-B
56 54
stormwater, permitted industrial discharges, atmospheric deposition, bank erosion, groundwater, and incidental releases (ibid). Extensive
17
samplings revealed significant sediment contamination, especially in 53
nearshore environments, and intermittent groundwater plumes (ibid).
19 52
The testing of surface water is notable in that it involved measurements
20
down to parts per qualdrillion (PPQ). 21
51
Timeline: • 1997 EPA Preliminary Assessment/Site Investigation • 2000 Portland Harbor Superfund Site Placed on National Priority List • 2001 Lower Willamette Group Members Sign Administrative Order on Consent • 2002 Remedial Investigation Round 1 Sampling Performed • 2004 Remedial Investigation Round 2 Sampling Begins • 2006 Remedial Investigation Round 3 Sampling Begins, Administrative Order on
23 49 48
50
22 47
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[DE]ACTIVE
25 46B
45
Consent Amended • 2007 Comprehensive Round 2 Site Characterization Summary and Data Gaps Analysis Report Submitted to EPA • 2009 Draft Remedial Investigation Report Submitted to EPA for Review • 2011 Draft Final Remedial Investigation Report Submitted to EPA for Review • 2011 Draft Feasibility Study Report Expected to be Submitted to EPA • TBD EPA Record of Decision and Post-Record of Decision Cleanup and Monitoring Activities
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46A
40-42
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39
38 37 36 26 32
27
31 30
28 29
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SCHNITZER -TERMINAL 5
A
Future Activations
Current hegemonic land uses are outlined in percentages. Graphed SMITH & BYBEE
temporal projections reveal potential future alterations and overlaps
B
Current and future usages
to increase productive economic, ecological and social space.
TYPOLOGIES TOYOTA LOTS
C
Smith and Bybee This is a Lake and wetland area that currently serves as a buffer/
B
ecological zone connected to the watershed of the north Portland ARKEMA & MCCORMICK
residential area.
D
Fallow
A
Lands that once were industrial but have since emptied and now SWAN ISLAND
lie vacant, often thronged with opportunistic grasses and invasives.
E
Interstitial spaces between the large scale industrial functions persist. Often characterized by under used industrial space with potential for greater layering.
ALBINA RAILYARD
Transitional industrial area
F
Areas where there is currently an industrial use that is either changing
n>
its function or will feasibly be succeeded by a different function.
WESTSIDE RAILYARD
Active industrial area 1
G
Areas of active industrial use of varying capacity (i.e. not fully optimizing the space in which it exists).
TANK FARM
D
Active industrial area 2
H
Areas of active industry that is heavily used on a regular basis (i.e. not likely changing in foreseeable the future).
FALLOW INDUSTRIAL
SOCIAL INDUSTRIAL
Reasoning
ECOLOGICAL
Schnitzer Steel — Terminal 5
E
H
PRESENT FUTURE
FUTURE ACTIVATIONS
C
Now
Smith & Bybee north PDX buffer
The space is characterized by large fallow interstitial conditions for
Fallow: inactive, no use
most of the year.
G
Transitioning Industrial Area
Future
Active Industrial Area Level 1
Industrial space is maximized and retrofitted with ecological
Active Industrial Area Level 2
F
University of Portland
22
infrastructure that provides access along varied edge conditions.
23
Smith & Bybee Lakes
Albina Rail Yards
Now
Now
Serves as an ecological buffer and low-use recreational park
A vast rail yard that currently functions as a parking space and
for north Portland.
maintance yard for the Burrlington Northern railroad.
Future
Future
The land has the potential to act as a high performance social and/or
Much of the storage needs of the rail yard should be moved to other
hydrological filter for the port and industrial processes.
yards away from the shoreline (i.e. Brooklyn Railyards to the south). New space can transition into other industries that can use the now
Toyota Lots
more spaced rail lines.
Now
ecological infrastructure can emerge.
a thoroughly layered space of industrial
transit, new industry, social infrastructure,
and accompanying
A transitional parking lot for cars between cargo ship and rail voyages that never reaches more than half capacity.
Westside Rail Yard
Future
Now
Industrial space is stacked temporally, allowing the maximization of
A long narrow extension of mixed industrial uses.
overlapping ecological and social infrastructure over a time spectrum.
These consist
of train yards, active industrial space, largely empty parking lots, warehouses, and many docks.
Arkema, McCormick & Baxter
Future
Now
Some of these industries should be consolidated in space as they
Fallow land is characterized by dirt, tire and debris mounds with
currently use more space than needed. In the large interstitial spaces,
waist high weeds and barbed wire fencing. All industry has left or
new social and ecological layered infrastructures could be built slowly
been razed, leaving only toxic traces in the ground.
over time. With a less flex able shoreline, more buffer spaces would need to be built into the near hydrology of the industries.
Future Intertwined ecological and social space that simultaneously treat
Tank Farm
and serve the university of Portland and neighboring communities (industrial workers and residents).
Now Significant numbers of very large chemical storage tanks exist in this
Swan Island
space. These tanks will most likely stay active.
Now
Future
Contributes significantly to the economic health of the city.
Extensive interstitial spaces exist between tanks that could be used for new infrastructures, social and/or ecological.
Future
Given the
importance of providing ecological buffers to the large tanks that
Poorly used interstitial space must be retrofitted and upgraded with
often have leaks or spills, a greater amount of ecological function is
ecological buffers/filters.
planned, rather than social.
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ENTROPIC INDEX
ENTROPIC INDEX
The entropic index is a graphical construct that speaks to the multiple
series which asymptotically approaches the quantity 0 without ever
trajectories within goal-driven indeterminate design processes. Read
actually equaling the quantity 0. However, at 2/27, the graph network
right to left, the drawing signifies the potential impact that minute
approaches a geo-spatial coordinate system which not only informs
design moves may have on larger landscape contexts and processes.
the branching pattern, but restricts its infinite geometric series to a
These impacts may be ecological, social, or health related.
specific locale.
The
drawing is constructed with a simple branching method, and informed by graph theory. Graph theory is generally used to calculate either the
The superimposition of the geometrically derived branching pattern
shortest route between two points (by nullifying alternate routes and
with the geographically specific drawing of the Port of Portland
arriving at the quantitatively shortest one) or to calculate connectivity.
suggests a multiplicity of metaphorical and analogical interpretations. At a pre-selected scale, certain regions were hatched (red, green, blue,
The first approach prioritizes line segments, while the second approach
yellow) to indicate design-phases in which certain processes might be
prioritizes nodes. In the drawing, the scale of both segments and
initiated. These processes are affected by previous decisions, while
nodes is reduced, left-to-right, at a regular geometric interval (2/(2n),
they also affect subsequent decisions. There is also an implication of
where n=i+1). That is, each successive geometric interval is half the
adaptive management strategies contained within the entire graphic.
size of its precursor. Therefore 1 becomes ½, which becomes Ÿ,
This implication is explored further in books Game-1, Game-2, Game-
etc. This perpetual halfing of scales produces a theoretical infinite
3, Game-4.
02
GAME 2 // TANK FARM
West Side Tank Farm
The west side tank farm is comprised of multiple industries and owners that take part in the collection and storage of a variety of chemicals. The storage facility retains chemicals that are pumped from ships, docked at one of two piers, through pipes to the tanks. From the tanks, chemicals are pumped into tanker cars in the adjacent railyard. Between these tanks, there is a considerable amount of interstitial space viable for potential reuse. Pedestrian insertions in the space occur. All insertions must account for the the need for utility vehicles to access these interstitial spaces between the tanks. How can entropy serve as a positive force within this circumstance? The tanks might change use in the future and create a new environment for plants as they are allowed to rust and fall apart. Newly derived spaces will allow for new connections to, and along, the shoreline.
03
GAME 2 // TANK FARM
WILLAMETTE
FIGURE 25’
WATER TREATMENT WILLAMETTE
04
05
Potential A: wetland insertion
A potential for the tank farm creates an integrated wetland cleansing and containment system in the interstitial spaces between the tanks and the underutilized space approaching the Willamette’s edge.
Script Node 1:
WATER TREATMENT
As a reflection of the sites use, circular collection ponds are built
WILLAMETTE
in these interstitial spaces between tanks. The water inverts the tank geometry, creating a shape that will quickly erode. Channels might then protrude along the ground underneath the transportation pipes, collecting runoff from the surrounding hills and from the tanks. The channels and ponds evolve, both as containment areas for future spills as well as planted remediation and treatment areas for chemicals and stormwater.
Possible future-Script Node 2: As the forms breakdown and the initial shapes spread, initial wetland processes form. Tanks are phased out and reused or taken over by plants in the area after cleaning and purging is completed. Future containment methods might allow for more thorough development of wetland spaces. Pedestrian pathways are safely built through the newly forming wetland, creating pedestrian and bike connections through the tank farm.
Possible Future-Script Node 3: Eventually the division between the land and the water begins to disappear. A developed wetland fills the voids between tanks and the Willamette. A developed ecotone exists in this space. Plants that have persisted in the tank farm, despite contamination from the tank spills, thrive. A new filter and buffer exists between tanks and the water where there wasn’t one before.
Alternate Possible Future Script Node: Drainage patterns change. A new development results in most of the water that was previously sheeting down the west hills to be diverted or collected in other areas. The wetland system drys up and becomes a dry collection system. Water holes are now simply spill containment areas. Blackberries run rampant.
06
GAME 2 // SCHNITZER STEEL
Schnitzer Steel
Schnitzer Steel is a major steel manufacturing and recycling corporation. Schnitzer’s main industrial facility is located in the northern reaches of the port of Portland.
The site covers
approximately 200 acres, much of which is comprised of infill over in the river. Site activities have resulted in large concentrations of heavy metals in the soil and groundwater. Antimony, zinc and mercury are the most prevalent. High levels of PAH’s and naphthalene are also present. Areas near the Willamette’s edge are regularly exposed to large quantities of metals while they are processed or prepped for processing in the recycling plant.
Schnitzer Steel
03
GAME 2 // SCHNITZER STEEL
04 05
SCRIPT NODE INITIAL STATE: The site protrudes over the Willamette with steep slopes descending down into the river. Inlets for barges extend down both sides.
Piles are driven into the site around the shoreline in order to support a structural deck.
06
A panelized steel deck is installed on piles, supporting industrial functionality above the plane of the soil.
Soil is loosened and shoreline processes are allowed to regenerate the site. Industrial functions continue above as ecological processes begin work on the soils below. Willows grow near the shoreline.
As industry is phased out and existing functions compete for space, deck panels are removed. Shoreline processes continue to seasonally flood into the site. Vegetation continues to colonize the new near shore habitat as willows and alders grow.
Deck panels are continually removed while vegetation continues its growth into the site.
07
GAME 3 // ALBINA
Albina Rail yard
The Albina Railyard is a 200 acre rail depot located directly on the Willamette below the bluffs just north of the Fremont bridge. The yard serves trains coming from inland and north, loading and unloading for the port as well as for “parking� in the extensive sidetracks before heading off on another trip. As a major feature of the waterfront it has no access for pedestrians. This is perhaps with good reason due to the dangers of trains moving around the area. The space is compacted earth and acts as a solid expanse of impervious soil with water sheeting off towards the Willamette. There are select areas of the site with containment methods that control runoff, but much of the site is exposed to contaminants. The site has had a history of fuel (diesel) spills in both contained and uncontained areas. The DEQ has found contaminated groundwater and soils throughout the site. While still a very active railyard, much of its function as a rail parking lot can, in the future, be transferred to another area, such as some of the large rail yards outside of the city that are not directly adjacent to the river, with less direct impact on a major river and away from such a central urban location. DIG STUDIO examined at how best to create insertions of entropy and ecological infrastructure into the overall scheme of a railyard. DIG STUDIO investigated the instigation of new ecotones on the site as well as the incorporation of pedestrian interactions with the site while maintaining the autonomy of the trains and the safety of people in proximity.
01
GAME 3 // ALBINA
SCRIPT TRAJECTORY SYMBOLOGY REMOVED RIPRAP; DECOMPRESSED SOIL FLOATING LAND DEBRIS COLLECTS CREATING OFFSHORE ISLAND WATER FLOWS CHANGE AND AREA DRIES UP MAJOR ENVIRONMENTAL SPILL> RAIL YARD SHUT DOWN FOR EXTEND PERIOD SEA LEVEL RISE> WETLANDS TURN INTO OPEN WATER> BOATING AMENITY BIOFUEL FARM IS NOT COST EFFECTIVE> WATER DEPTH MANAGMENT FOR GREATER ECOTONE GRADIENT
ROOT BAG DISSOLVES
@ CONSTANT RATE
SHORELINE SCORE CONDITION: CONTAMINATED RIVER SEDIMENT
SHORELINE SCORE A INSERTION: ROOTED BIOCELL
CON TA MI N A TED G ROU N D WA TER
ROOT BAG DISSINTEGRATION; BIOCELL IS MADE MOBILE 1
FALLOW SCORE A INSERTION: NANOTUBES & BIRCH PLUME
RIPRAP EDGE CONDITION
1
SHORELINE SCORE A INSERTION: AUTONOMOUS BIOCELL
CON TA MI N A TED G ROU N D WA TER
FALLOW SCORE A INSERTION: NANOTUBES & BIRCH PLUME
BLUFF_RAILYARD CONDITION
+ + + + +++ + +
+ + +++ + + + + + ++ + + + + + + + +
XX XX
+
X
XX XX
FALLOW SCORE CONDITION: CONTAMINATED GROUNWATER _FIELD
X
XX
X
XX X
X
XX
X
XX
X
X
RAIL SCORE INSERTION: GMO POPLARS
WASTEWATER IN
BIOFUEL/ CLEAN WATER OUT XXX
XXX
XXX XXX
XXX
XXX
XXX
RAIL SCORE CONDITION: CONTAMINATED SOIL
RAIL SCORE GMO POPLARS ARE SUCCEDED
Potential A: Rail Script Score
One potential for the rail yard involve small ecological insertions between the tracks. Many of these insertions may be paired with existing tracks that have considerable space between them. Other insertions can pass between the areas of tracks that are feasibly able to move elsewhere as the railyard evolves and changes over time.
Script Node 1: Vertically dig trenches with steep sides, cut out the compacted soils and set up conditions for controlled erosion to loosen further soils. This allows plants to inhabit the soil.
the trench and water to penetrate
Poplars that are modified to break down the oil based
contaminants in the soil are planted in and near these trenches where
XXX
XXX
XXX XXX
water will naturally collect and percolate into the soil to the poplar
XXX
XXX
XXX
RAIL SCORE CONDITION: CONTAMINATED SOIL
root systems. These poplars effectively stop contamination plume from progressing towards the Willamette. Rail tracks that are phased out are converted into pedestrian paths, equipped with new vertical supports that tolerate erosion around them.
Possible future-Script Node 2: Poplar roots overtake the ground, forcing erosion and water incursions. Areas of hydrocarbon pollution are treated in the roots of the poplars and in time remediated. Swaths of poplars are succeeded by wetland plants after chemicals are gone. Wetland plants such, as willows, can now be farmed to function as fuel sources for locally oriented power plants. Effluents are piped and treated in the wetlands spaces within
XX XX
the rail yard while the remaining tracks have a buffer between them
X
XX XX
XX
X XX
X
X
XX
X
X
XX
X
X
RAIL SCORE INSERTION: GMO POPLARS
and the Willamette river. The Pedestrian paths becomes a marker for changes as erosion removes soil from below them and exposes the pathway’s structural support system. In time, an elevated path is created.
Alternate Possible Future Script Node: Water currents change or diverted and thus, not much drainage occurs on-site. The wetlands dry up and the poplars and willows
WASTEWATER IN
die out or are succeeded by upland species, or blackberries. Bird habitats form in these new plant areas. Surface pathways continue
BIOFUEL/ CLEAN WATER OUT
for pedestrian and bike connections.
RAIL SCORE GMO POPLARS ARE SUCCEDED
03
Potential B: Shoreline script Score
Shoreline segments are often contaminated and in need of remediated. Phytoremediation methods are used to remove toxins and promote near shore habitats and ecotones.
Script Node 1: Biocells, or stand alone phyto/soil conglomerations are rooted near the shore and function as filters of river water that enters near the shoreline. The Biocell, while rooted into the embankement sediment ,break down organic contaminants and remove heavy metals.
Possible future-Script Node 2: An anchor holding the cell near the shore dissolves at a set rate.
SHORELINE SCORE CONDITION: CONTAMINATED RIVER SEDIMENT
After breaking down hydrocarbons in its rooted location, the island is allowed to float away to another location, effectively guided by currents to location that is in need of remediation. The biocell is rerooted to the embankment, and begins again.
Alternate Possible Future Script Node: Biocells that are deployed across the region collect in a single location downstream. These cells create a new island in the channel which becomes a home for homeless individuals.
ROOT BAG DISSOLVES
@ CONSTANT RATE
SHORELINE SCORE A INSERTION: ROOTED BIOCELL
ROOT BAG DISSINTEGRATION; BIOCELL IS MADE MOBILE
1
SHORELINE SCORE A INSERTION: AUTONOMOUS BIOCELL
04
McCormick & Baxter
The site comprised of McCormick & Baxter and Triangle Park are located at the base of Waud Bluffs on the eastern side of the Willamette River, between river miles 6.4 and 6.8, within the larger Port of Portland Superfund Site. Their industrial histories can be traced back to the early twentieth century, and include ship building, railroad maintenance, wood treatment, a toxic-spill clean-up company, and chemical storage. The fluvial geomorphology of the site is highly suggestive of a continuous topographical fabric, over a continuous water table. However, in practice, these sites have been treated separately, despite the continuous nature of the space in which they reside. For example, McCormick and Baxter happened nearly a decade before Triangle Park This is due in part to liability issues that resulted in Triangle Park being designated an ‘orphan fund’ site by the Oregon DEQ, in order to fund remediation work done there. Triangle Park does not appear to have been included under EPA’s official superfund listing. The continuous tenure of the McCormick & Baxter Creosoting Company, from 1944-1991, at the north end made its clean-up more straight forward than that of the south end, which has a more tumultuous ownership history. The areas serve a similar function now that neither site has any buildings or industry on them. Despite these spaces were divided into two tax lots with varied histories, the future invariably should hold these sites together as one space. Natural processes function across these arbitrary boundaries for thousands of years due to its location at the bottom of the Waud Bluffs. The site is located on an area that was constructed by placement of borrowed material, perhaps including dredged material, along mile 7 of the Willamette River during the early 1900s. The site is generally flat and lies between a 120foot high bluff along the northeastern border and the Willamette River to the southwest. A sandy beach along the river is exposed during the majority of the year but is submerged during high river stages that typically occur in the late winter and early spring.
McCormic & Baxter Superfund Site & Triangle Park.
Surface elevations on site range from 29 to 36 feet above mean sea level (MSL) with the land surface sloped toward the river. The site also includes 15 acres of river sediments. Fill that is composed of fine to medium grained sands, with areas near the TFA (tank farm area) also consisting of sawdust and wood chips, extends for 20 to 30 feet below ground surface. Alluvial sand and silt deposits exist beneath this fill and have a thickness of nearly 100 feet near the bluff to the northeast and 0 feet in places near the river to the southwest. Beneath the silt layer is an intermediate aquifer that varies in thickness. In the central process area it is 12 feet thick and in the TFA, where the overlying silt layer is over 100 feet thick, it is nonexistent. Near the river, this intermediate zone is connected with the deeper zone which is primarily alluvial sands consisting of fine to medium grained alluvial sand. This intermediate aquifer is approximately 50 feet thick and is hydraulically connected to the deeper aquifer near the river. Groundwater in the area is generally 20 to 25 feet below ground surface and flows toward the river during much of the year. Reversal of flow from the river toward the site occurs near the river during high water periods in the late winter and spring when the river stage is higher than the groundwater elevation.
02
Network Map
GRASS Q
~+
SCRIPT TRAJECTORY SYMBOLOGY
HEALTH SYMBOLOGY
BIRCH PLUME PROVIDES PERCHING SITES, > SECONDARY PLUME IS VIA SEED DISPERSAL
BARGE X, Y & Z LEFT TO RUST> IRON PLUME
BARGE INSERTED INTO BLUFF> BLUFF PIER
BARGE BURNERS>
POTENTIAL FOR UN-HEALTHFUL OUTCOME POTENTIAL FOR HEALTHFUL OUTCOME TREE Y
p
BREAK CAP
TREE X
INCREASE
GRASS Z 1
FALLOW SCORE A INSERTION: PLUME; RIGID PATH
FALLOW SCORE INSERTION: PLUME; RIGID PLAN A
q
DECREASE
CAP BROKEN GRASS Q
TREE X
~
~ GRASS Q
~
+
BARGE
TREE Y
~
~
~
~
AND EDGE CONDITIONS
XXX
XXX
XXX
XXX
RIVER SCORE CONDITION: CONTAMINATED RIVER SEDIMENT
~
q TOUCH
POINTS
~
+ +
p HUMAN VECTOR PATHWAYS
ATTENTION
~
GAME 4 // McCORMICK & BAXTER
X1YR
TREE Y
PLUME X
PLUME Y
SURVEYED EDGE
SURVEYED EDGE
PLUME X
~
+
p GENTRIFICATION
p NEIGHBORHOOD AMENITY
+
1
SCORE A FALLOW SCOREFALLOW INSERTION: PLUME; INSERTION: PLUME; RIGID PATH RIGID PATH A
2
PLUME Y
+
+
+
X
ILLNESSES
+
Y
p MENTAL WELLBEING
q CHRONIC
+
FALLOW SCORE A INSERTION: PLUME; SUBSET INTRUCTIONS: RIGID PATH REPEAT STEPS 1-3 EVERY 12 MONTHS REPEAT.REPEAT.REPEAT
+
q CRIME
SURVEYED EDGE
SURVEYED EDGE
~
+
p ECONOMIC DRAW
SURVEYED EDGE
+
PLUME X SURVEYED EDGE
FALLOW SCORE B INSERTION: PLUME; FLEX PATH
3
FALLOW SCORE B INSERTION: PLUME; FLEX PATH
X
WETLAND
+
FALLOW SCORE INSERTION: PLUME; SUBSET INTRUCTIONS: RIGID PATH REPEAT STEPS 1-3 EVERY 12 MONTHS
+
+
2-1
FALLOW SCORE RIPARIAN FLOOD PLAIN
2
Z
+
PLUME Y SURVEYED EDGE 2
REPEAT.REPEAT.REPEAT
+
+ X3YR
+
X5YR
RIVER SCORE FALLOW SCORE B INSERTION: PLUME; PLUME X SURVEYED EDGE FLEX PLAN 3 FALLOW SCORE B INSERTION: PLUME; FLEX PATH
+
A
Y3YR
+
~
2
FALLOW SCORE B INSERTION: PLUME; FLEX PATH
~ + +
~
X5YR
~
PLUME X SURVEYED EDGE 3
FALLOW SCORE B INSERTION: PLUME; FLEX PATH
03
+
~ +
+
Y
Z
SUBSET INTRUCTIONS: REPEAT STEPS 1-3 EVERY 12 MONTHS REPEAT X 5YR. PLUME X OVERTAKES PLUME Y
1
SURVEYED EDGE
+ X
RIVER SCORE A
PLUME Y
SURVEYED EDGE
~
+
+
PLUME X
+ +
~
+ +
Y
A
Y1YR
PLUME X SURVEYED EDGE
p MENTAL WELLBEING
+ +
Y
+
+
p SENSORY STIMULATION
Y
X
q STRESS
p CURIOSITY ABOUT SITE
POINTS
X5YR
+
PLUME Y p TOURISM 2
Z
+
+
p TOUCH
SUBSET INTRUCTIONS: REPEAT STEPS 1-3 EVERY 12 MONTHS REPEAT X 5YR. PLUME X OVERTAKES PLUME Y
Y3YR
SURVEYED EDGE
+
+ X
p ENVIRON. STEWARDSHIP
PRIDE
PLUME X
p PROPERTY VALUES
AMENITY
+
+
p JOBS Z
+
pNEIGHBORHOOD
+
+
Y
2-1
FALLOW SCORE RIPARIAN FLOOD PLAIN
Z
+
+
+
p HABITAT
2-1
FALLOW SCORE RIPARIAN FLOOD PLAIN
X
p PROPERTY VALUES
p COMMUNITY
SUBSET INTRUCTIONS: B. PLANT PLUME NODES 1. SURVEY EVERY 12 MONTHS FOR EDGE DELINEATION (PLANT HEIGHT & CONCENTRATION ) Z 2. INSTALL ELEVATED MODULAR GRATE PATH AT EDGE 3. @1 YEAR: REMOVE & REINSTALL PATH AT NEW SURVEYED EDGE SUBSET INTRUCTIONS: REPEAT STEPS 1-3 EVERY 12 MONTHS REPEAT STEPS 1-3 EVERY 12 MONTHS REPEAT X 5YR. PLUME X OVERTAKES PLUME Y
~
p BIODIVERSITY
SERVICES
LAB
+
p WALKABILITY
X3YR
PLUME Y
~
+
p FUNCTIONING
SURVEYED EDGEECOSYSTEM 2
FALLOW SCORE B INSERTION: PLUME; FLEX PATH
COLONIZATION
+
~
q SOCIAL ENGAGEMENT
Y3YR
SURVEYED EDGE
FALLOW SCORE B INSERTION: PLUME; FLEX PLAN
GRASS Z
+
p SOCIAL COHESION
Y1YR
PLUME X
X1YR
~
X3YR
+
~ RIVER SCORE INSERTION: NANOBUCKS> JETTY
+
Y1YR
p LEARNING
~
p INJURIES
Y
FALLOW SCORE B INSERTION: PLUME; FLEX PLAN
p REGULATORY
A
+
p SOCIAL JUSTICE
FALLOW SCORE A INSERTION: PLUME; RIGID PLAN
+
p PEOPLE ON SITE
Z
p CHRONIC ILLNESSES
XXX
+
PATHS
p ACCESSIBLE
SUBSET INTRUCTIONS: B. PLANT PLUME NODES 1. SURVEY EVERY 12 MONTHS FOR EDGE DELINEATION (PLANT HEIGHT & CONCENTRATION ) 2. INSTALL ELEVATED MODULAR GRATE PATH AT EDGE 3. @1 YEAR: REMOVE & REINSTALL PATH AT NEW SURVEYED EDGE REPEAT STEPS 1-3 EVERY 12 MONTHS
~
WILLAMETTE RIVER EXISTING RIVER SEDIMENT
BARGE ON END
2
~
p MENTAL WELLBEING
Y
Z
SUBSET INTRUCTIONS: REPEAT STEPS 1-3 EVERY 12 MONTHS REPEAT.REPEAT.REPEAT
FRAGMENTED LANDSCAPES
~ X
X
Y
X1YR
p RECONNECT
DERELICT BARGES ARE USED AS MARKERS FOR CHANGE, AND SUPPORTS FOR NEW PED/BIKE INFRASTURCE
~
~
q ECOTONES
XXX
TO ADVERSITY
TREE X
~
FALLOW PATCH MCORMICK & BAXTER, ARKEMA
q BIODIVERSITY
CAP
2-1
FALLOW SCORE RIPARIAN FLOOD PLAIN
Z
SUBSET INTRUCTIONS: B. PLANT PLUME NODES 1. SURVEY EVERY 12 MONTHS FOR EDGE DELINEATION (PLANT HEIGHT & CONCENTRATION ) 2. INSTALL ELEVATED MODULAR GRATE PATH AT EDGE 3. @1 YEAR: REMOVE & REINSTALL PATH AT NEW SURVEYED EDGE REPEAT STEPS 1-3 EVERY 12 MONTHS
+
ADDITION
+
2
FALLOW SCORE A INSERTION: PLUME; RIGID PATH
q STRESS
p RESILIENCY
p EDUCATION
RIVERBED
~
~
FALLOW SCORE A INSERTION: PLUME; RIGID PATH
+
+
+
GRASS Q p HUMAN VECTOR PATHWAYS
POINTS
EXISTING R A I L BRIDGE
~
qFUNCTIONING
+
p SENSORY STIMULATION
X
~
+
p TOUCH
q ENVIR. STEWARDSHIP
XXX
~
+
WILLAMETTE WATER
~
1
p INJURIES
~
ECOSYSTEM SERVICES
~
+
FALLOW SCORE A INSERTION: PLUME; RIGID PLAN
1
FALLOW SCORE A INSERTION: PLUME; RIGID PATH
p MENTAL WELLBEING
GRASS Z
BARGE ON END
q FUNCTIONING
+
GRASS Z
FALLOW SCORE A INSERTION: PLUME; RIGID PLAN
~
ABANDONED
~
TREE Y
TREE X
~
Insertion: Ped/Bike Connect
BARGE ON END
Health impacts potential EXISTING R A I L BRIDGE
ADDITION
WILLAMETTE WATER
+
RIVERBED
+
p ACCESSIBLE
DERELICT BARGES ARE USED AS MARKERS FOR CHANGE, AND SUPPORTS FOR NEW PED/BIKE INFRASTURCE
BARGE ON END
p SOCIAL JUSTICE
PATHS
+
+
p PEOPLE ON SITE
+
p WALKABILITY
+
q CHRONIC ILLNESSES
~
+
p SOCIAL COHESION
p GENTRIFICATION
p NEIGHBORHOOD AMENITY
+
p MENTAL WELLBEING
+
q CRIME
+
p PROPERTY VALUES
Deconstructed derelict barges are proposed to be used as supports
To follow one chain of events that are a potential cascade from this
and pieces to build new infrastructure. There is a plethora of old
insertion: the pedestrian connection is built and creates greater
barges around the harbor with the potential for reuse and recycling.
access for people without other means of transport (p ACCESSIBLE).
In this proposition barges are used for their length and structural
This leads to greater social justice for the communities (p SOCIAL
capacity to create a line of supports to build a new bike pedestrian
JUSTICE).
bridge extension next to the existing rail bridge. Pieces of the barges
increased value to lands in the neighborhood (p PROPERTY VALUES). This
could are cut and rearranged to create “follies” through the water
can then lead to gentrification (p GENTRIFICATION).
and the site that create a visual phenomenon for site visitors and the passengers on the amtrak trains that go across this bridge every day.
+ - ~ Symbols are
Within the Potentiallity Matrix is a set of smaller keys that reference the potential health affects of a given insertion.
used to represent the overall effects of each insertion and then the cascading potentiality is shown in consecutive circles representative of moments in time.
REUSED/REBUILT BARGE FOLLIES
04
With greater equality crime can decrease (q CRIME). Leading to
GRASS Q
TREE X
Potential A: Rigid Plan
As a fallow field the McCormick and Baxter site has the potential to create dynamic relationships between planted materials that are working to remediate the soils and groundwater and the site users
GRASS Q
moving through the site.
TREE Y TREE X
Script Node 1:
GRASS Z 1
FALLOW SCORE A INSERTION: PL RIG
FALLOW SCORE INSERTION: PLUME; RIGID PLAN
A network of rigid paths and walkways are constructed through the
A
site. Along with these are nodes of planted insertions with relationship to the groundwater plumes. These can be modified poplars or other plants that succeed them.
TREE Y
GRASS Z GRASS Q Possible future-Script Node 2:
FALLOW PATCH MCORMICK & BAXTER, ARKEMA
The Rigid Path plan becomes a datum for the changes and TREE X
FALLOW SCORE A INSERTION: PLUME; RIGID PLAN
movements that happen around the site. Trees would move with the groundwater plumes as they gain greater nutrients from the broken down hydrocarbons. Grasses will plume out as well and continue the work of the trees. GRASS Q TREE Y
Possible Future-Script Node 3: GRASS Z
TREE X
1
In time the soils are returned to a functional state with low compaction FALLOW SCORE A INSERTION: and greater organics.PLUME; The high water table in relation to the land will RIGID PLAN lead to a return of the flood plane and marshlands on the fallow area.
FALLOW SCORE A INSERTION: PLUME; RIGID PATH
The ridgid path will remain and allow for a continued relationship
TREE Y
between the landscape and the user. GRASS Z
FALLOW SCORE INSERTION: PLUME; RIGID PLAN A
2
FALLOW SCORE A INSERTION: PLUME; RIGID PATH
1
2
FALLOW SCORE A INSERTION: PLUME; RIGID PATH
2-1
FALLOW SCORE RIPARIAN FLOOD PLAIN
2
FALLOW SCORE A INSERTION: PLUME; RIGID PATH
05 2
2-1
FALLOW SCORE FALLOW SCORE A RIPARIAN FLO INSERTION: PLUME; PL RIGID PATH
2-1
Previous Remediation Efforts
These sites have lain fallow for nearly a decade, and continue to contain nothing within them aside from fences, train tracks, and piles of dirt. McCormick and Baxter had extensive work completed in an attempt to contain and mitigate the environmental impact of contaminants on the site. Triangle Park was recently acquired by the University of Portland for expansion of sports fields. Together, McCormic & Baxter and Triangle Park comprise 115 acres of contaminated soil, sediment in addition to groundwater. Twenty three nearshore acres of these have been capped with riprap and flexible concrete mats. Forty one acres at McCormic & Baxter were remediated between 1990 and 2005, with a preliminary close-out report issued. The close-out report summarizes actions taken at McCormic & Baxter. Nearshore: • • • • • • • • • • • • • • •
Total area: 23 acres Pilings removed: 1601 Solid waste removed: 2700 tons Staples removed: 87000 Sediment cap area: 14.7 acres 130,944 tons of sand placed 600 tons of organoclay placed 7,200 tons of ACB 12,585 tons of filter gravel 23,250 tons of 6 inch rock armoring 23,300 tons of 10 inch rock armoring 568 tons of riprap 9,914 tons of sand overlay 30,000 tons of topsoil Total tonnage; 215,000 tons (430,000,000 pounds)
Upland impermeable cap: • • • • • • • •
8,000 cubic yards of sand used as a leveling-layer about 4 inches thick. 72,000 square yards ofhigh density polyethylene (HDPE) geomembrane liner. 72,000 square yards of a geocomposite plastic ‘fabric’ that allows water to flow laterally. 47,000 cubic yards of sand of varying depths to allow for drainage. 12,000 cubic yards of 4”-minus crushed rock forming a screened biotic barrier layer approximately 6 inches thick. 72,000 square yards of geotextile filter fabric. 24,000 cubic yards of topsoil placed approximately 9 to 12 inches in depth. 20 species of native grasses to provide a diverse and sustainable herbatious cover in order to minimize surface erosion.
Subsequent monitoring revealed continued seapage of NAPL (nonaqueous phase liquids, compounds that do not dissolve in water) into both the river and nearshore environment, despite $22M in remediation, including groundwater pumping, filtering, excavation, and capping. In 2008 The University of Portland (located 135 feet above atop the Waud Bluff) purchased Triangle park, with plans for future athletic facilities. The University is also working towards closing a deal for the McCormic & Baxter site.
06
>
PREVIOUS REMEDIATIONS N
07
McCormick & Baxter Insertions and Health
The plan for McCormick and Baxter compresses a time spectrum into a single map.
The initial insertions, grading and structures,
are mapped in the strongest most rigid lines as they are the known element in the site at T=0.
Along with these rigid lines are the
intentions of each insertion made evident by mapping the script that ties to the plan. The traditional method of showing the future through multiple maps inherently contains elements of prescriptiveness with the belief that one’s initial design will always produce a specific end. This method reveals the true nature of designing over time and the uncontrollable nature of doing so. Layered with the rigid linework are colored washes representing T=X. These are the indeterminate plumes, across the site and potentialities that exist in the insertions. The plumes are the insertion of a single or group of elements and how through natural forces it then spreads across the site. The final shape of the plume is entirely driven by the natural processes and unforseen events of the future. Each color scheme represents different plumes whether it be planted plumes, errosional plumes, or movement plumes. The quality of the wash speaks to the unknown nature of these expanses versus the hard lines of the initial installation with its ridgid knowledge of placement. With the combination of diagrammatic and sectional descriptors of process insertions and layered plume mapping we are creating/ exploring ways to make dynamic a form of communication that is often static without creating a series of consecutive maps.
This
method is an attempt to speak to the indeterminate and dynamic nature of a site all at once. On the following page is a second iteration of the plan looking at the potential health affects of different script insertions. The initial scripts are justified to the right of the plan and point to an example point of insertion. To the left are potential health responses to the insertion. This is a compression and description of an indeterminate future. The health outcomes are at T=X while the insertions are at T=0.
08
RAIL CONSTANT
SEC T RAIL LAB
HYPERACCUMULATOR WALK BARRIER CAP AND WALL (STRATEGICALLY REMOVED) Pb
+
Pb
=
Pb Pb
Pb
Cl
=
+
Cl
CHEMICAL
& H
H C
Cl
C
Cl
+
As
SEQUESTRATION
C
=
FERN
ENDOPHYTE++
POPLARS
SHORE PINE PLANTING
H C
BIODEGRADATION
H
ACCUMULATION
30FT
POPLAR PLANTING
Pb
SEQUESTRATION
Pb
Pb
20FT
20FT
60째
BIRCH & ASPEN PLANTING
20FT
FT
15
15FT
WETLAND SPORE T1
+
GROUNDWATER
= NANOTUBE
+ WASTEWATER
EFFLUENT
= WILLOW
BIRCH
, INDETERMINANTGAMEFIELDS
BTEX
PAH
+
=
Cd
BTEX PAH
Cd
HEAVYMETAL ORGANICCHEMICAL
BTEX
PAH
& H
H
Cd
C
BTEX PAH
Cl
C
Cl
BIODEGRADATION OGRANICCHEMS
=
+
BIND+SEQUESTER
Cd
Cd
REMISLAND
Cd
HYDROLOGIC PLUME
BIRCH/ASPEN PLUME
09
POPLAR PLUME
CLEANSED WATER
+ + + + +++ + + + CONTAMINATED
EFFLUENT TREATMENT BIOFUEL PRODUCTION STORMWATER DETENTION
BARGE ROOM
FILTER+DEGRADE
WETLAND SPORE T2
n>
MCCORMICK & BAXTER
A,B
REUSED/REBUILT BARGE FOLLIES
MENTALWELLBEING
-$ +$ -$
-$
INSTALL SCRIPTS
+$
PHYSICALHEALTHCHRONICILLNESSES
+
= PUBLIC ACCESSIBLE
C
C
Cl
=
+
Cl
+$
MONOCULTURE
30FT
H
H C
C
Cl
=
+
Cl
& H
H C C
Cl
Cl
BIODEGRADATION
H
POPLAR PLANTING
+$ H
ACCUMULATION
EDUCATION INSPIRATION
RESEARCH JOBS
REUSED/REBUILT BARGE FOLLIES
MENTALWELLBEING
REUSED/REBUILT BARGE FOLLIES
20FT
ENDOPHYTE++
CHEMICAL
POPLARS
ENDOPHYTE++
CHEMICAL
POPLARS
= PUBLIC ACCESSIBLE
EDUCATION PROCESSES
Pb
Pb
+
As
= +$
FERN
HEALTHY SOIL
HABITAT
+
Pb
=
Pb
Pb Pb
+
As
SEQUESTRATION
+$
RESEARCH JOBS
Pb
Pb
=
+
SHORE PINE PLANTING
FERN
20FT
= REFLECTION STEWARDSHIP
+
=
Cd
REMISLANDCONFLICTS
15FT
PUBLIC ACCESSIBLE
REFORESTATION HABITAT
FT
15
60째
CLEANWATER FLOATINGHABITAT
=
+ HEAVYMETAL ORGANICCHEMICAL
REMISLAND
BIND+SEQUESTER
Cd
& H
H C
Cd
Cl
PAH
C
Cl
BIODEGRADATION OGRANICCHEMS
PATHWAY REVEALED
BIRCH & ASPEN PLANTING
+
EROSIONACCUMULATION NEARSHOREHABITAT
SEQUESTRATION
EROSIONTURBIDITY AQUATICUNHEALTH
20FT
PUBLIC EDUCATION
-$ +$ -$
-$
COMMUNITYUNIVERSITY
PARTNERSHIPS
-$
SEDIMENTATIONAQUATIC HEALTH
PROPERTYVALUES
NEIGHBORHOODAMENITY
= NANOTUBE
, INDETERMINANTGAMEFIELDS
+ WASTEWATER
EFFLUENT
= WILLOW
BIRCH
+$
DECONTAMINATIONAQUATIC HEALTH
-$ +$ -$
-$
+$
MENTALWELLBEING
BIRCH
+$
+$
+
GROUNDWATER
PHYSICALHEALTHCHRONICILLNESSES
ECOSYSTEMSERVICES
WILLOW
+$
+
CONTAMINATED
CLEANSED WATER
NANOTUBE
+ + + + +++ + +
EFFLUENT TREATMENT BIOFUEL PRODUCTION STORMWATER DETENTION
+$
+
MENTALWELLBEING
=
FILTER+DEGRADE
RESEARCH JOBS
FILTER+DEGRADE
CLEANSED WATER
+$
PHYSICALHEALTHCHRONICILLNESSES
HYDROLOGIC PLUME BIRCH/ASPEN PLUME POPLAR PLUME
n>
MCCORMICK &BAXTER HEALTH
POTENTIAL HEALTH OUTCOMES
Transects
The sections show a multi step process for how we propose to instigate one of the primary acts on the site. This move is to break open the containment walls that were put in place during the early remediatory efforts. We have graded the site so that surface water is channeled into infiltration points towards the bluff side of the site.
From there the water flushes through the contaminated soils
and pushes it into the plumes of poplars which can then proceed to break down and clean the contaminants in the water and prevent the pollutants from seeping out into the river.
12
TRANSECTS
A
B
Insertion A
Along with phytoremediatory methods there are techniques that use new technologies to clean water. The “nano tubes� are large rods
Nano tubes
filled with nanotechnology cleansers which are able to collect the impurities out of water that passes through them. By placing the nano cleansers in large tubes, which are inserted into the ground, capillary action can pull water upwards out of the ground. As water is pulled up, it is cleansed in the process before it is released. Light may also be emitted to signal this cleansing process. The tubes then function as indicators expressing the amount of toxins that are pulled from the ground. These tubes can be placed in a meaningful
+
CONTAMINATED
+
GROUNDWATER
= NANOTUBE
14
CLEANSED WATER
+ + + + +++ + +
FILTER+DEGRADE
way around the site in a method to expose the cleaning to passers by.
Insertion B
Derelict barges in the port may also become a complex set of structures off the shore. These structures become classrooms or general viewing
Barge Reuse as underwater viewing laboratory
stations for the conditions of the water that are passing by the site. A glass insertion in the old barge creates the space. The use of the barge creates a connection to the industrial heritage of the site while also exploring new productive uses of these vessels.
15
Site Views
Topographic renderings of the site show some of the relationships between the site, the water, and the bluffs above. Pictures of the constructed topographic model also help to show the larger grading moves that help to kickstart the processes on the site.
16
17
DEFINING AND AIMING FOR HEALTH IN DESIGN
HEALTH AS THE GOAL
01
DEFINING AND AIMING FOR HEALTH IN DESIGN
HEALTH AS THE GOAL
Introduction
might still degrade. Furthermore, if you have a low
Health as the Goal Why is health so important?
socioeconomic status, or do not have convenient A deep biological
yearning for survival drives our need to be healthy as a species. But this instinct does not always overrule our desire or ability to be healthy, regardless of our genetic predispositions. Intuitively, if we have lived at all, it is something
Health is often misunderstood as being a direct result
we seek and value”
of genes and behavior choices.
We often believe
that our everyday actions will directly correlate with health outcomes. If you eat your carrots, you will have good eyesight. Unfortunately, health is much more complex than a simple “do this and get that” philosophy. It is true that carrots contain Vitamin A which strengthens eye tissue and is important in eyesight maintenance, however you could eat carrots every day, but if your job forces you to stare at a computer screen for 8 hours straight, or you are always driving at night because of your family schedule, your eyesight
02
buy the carrots or other food options necessary to strengthen your eyes. For these reasons, health can often be seen as a symbol of control, power and accomplishment, which is evident in the physical environment we live in.
“Health is not just a term to be defined.
~Daniel Callahan
access to healthy food stores, you are not able to
Instead of a static masterplan as the goal The effect of the built environment on health is just
of a design, could ‘health’ be the goal?
as complex, if not more, than dietary choices. Just because your neighborhood has a sidewalk and tree lined streets does not mean that you are necessarily going to walk every day and maintain a healthy weight, thwarting off diabetes and heart disease. It might, however, mean that the environment is not getting in the way of desires or abilities to be healthy, and in fact might help to inspire healthy choices. The following pages explore what health is, the relationship
between
health
and
the
physical
environment and how this relationship fits into design practices. This section asks the question:
03
Varying Perspectives
Health Entanglement
Webster defines health as “free from illness, injury
WHO’s and Bircher’s views of health magnify beyond
or pain.”
The World Health Organization (WHO)
one’s personal state and implies a connectedness
expands this definition to the “state of complete
to external factors, such as social systems. Many,
physical, mental, and social well-being and not
if not all aspects of life influence one’s ability to be
merely the absence of disease or infirmity” (WHO,
healthy. For example, a person’s inability to afford
1946), implying a relationship between a functioning
medicine may transform a common illness into a
body and personal happiness. Johannes Bircher, in
long term battle for survival. The struggle with illness
response to global health practices, allows for an
may affect relationships with family and friends, and
individual health value system based on culture, age,
in turn his financial and mental support system. If
and life values in his definition “a dynamic state of
his or her house lacks tree cover protection or he or
wellbeing characterized by a physical, mental and
she cannot afford air conditioning in a heat wave,
social potential, which satisfies the demands of a
he or she may heal more slowly or develop further
life commensurate with age, culture and personal
illnesses that may exacerbate his or her condition.
responsibility” (Bircher, 2005).
economic health
local
sonal er
ecological health
physical health
For these reasons, health should be viewed in a much
Cultural acceptance,
more holistic sense, understanding that economic
geographic conditions, personal standards, and
systems, social fabrics, ecological function and
clinical diagnoses may all influence how one views
general well-being are directly linked with physical
his or her health and wellbeing.
and mental health.
This holistic view of health
implies a relationship between people, landscapes and ecological systems, and understands that health spans multiple scales of personal, local, and global. 04
civic health
environmental health
As the definition
of health continues to evolve it becomes clear that health can be subjective.
bal g lo
p
Defining Health
05
holistic health for landscapes, people, ecologies
social health
spiritual health mental health
pos
sibl
Because of its deep intertwined connectedness and
Health Complexity
expansive ramifications, health requires constant evaluation and reflection.
Health is constantly evolving and is difficult to
This evaluative process
is necessary to identify emerging unhealth and
predict. Mapping out past health relationships is
problem solve for positive interventions to improve
significantly easier than the current state due to the
health.
reliability of retrospective analysis. Nonetheless, a
Evaluation of holistic health, however is
not an easy task. It spans multiple disciplines and
general understanding of how the various aspects
bodies of knowledge. It requires both quantitative
of health are connected will help determine what
and qualitative data collection.
solutions may have the greatest overall positive
Furthermore, it
requires baseline perspective and a standard of
effects.
comparison, to determine what is indeed healthy or unhealthy. As mentioned earlier, this health standard is often personalized based on culture, age etc. and so therefore needs to be contextual and specific to the situation. When applying health evaluation to the design of a landscape, for example, it may be best to define health through the goals of the project involving commmunity desires and needs, and not simply a regulatory standard. The diagram to the right displays that while it may be easy to determine what is un-health, there are varying degrees of health standards.
06 Ramifications [yWorks, yFiles Visualization]
sult
}} } { { {
ealth
un-h
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ants
} { } }} {{{ }{
ess
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07
un-
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Defining Health in Landscape Design
Community
Defining Health in IndustriallyModified Sites
plays
a
big
role
in
industrially-modified areas. Even if a site has been decontaminated, perception of unhealth reduces
Landscapes can be indicators of health. Because they are imprinted by cultural desires, economic
Those sites and people that have been affected by
conditions, natural processes and human impact
industrial processes exemplify particularly dramatic
throughout history, they are both time capsules
health conditions. These industrially-modified sites
and barcodes suggesting health and unhealth.
are damaged. The damage transcends boundaries
Landscapes can also influence health.
and professions through plumes of economic, social,
They can
perception
regulate local climate and property values. They can
political and environmental destruction.
provide resilience or hazard to natural disasters and
itself, its surroundings and its global neighbors,
can facilitate social bonding. They can provide clean
industrially-modified sites often have numerous
air, water, soil and food, and can inspire mental
health impacts to landscapes, people and ecologies.
wellbeing and positive perception.
These residuals are often measured as isolated issues
real estate values, increases crime, and lessens neighborhood pride, all of which affect individual and community resilience to life challenges. Post industrial sites leave incinerating holes in the community fabric. These holes are visual reminders
Toxic to
of economic prosperity, collapse and failure. They are cultural graveyards of past everyday life and often create physical boundaries that reduce current opportunities.
by specialized experts, causing conflicting strategies Because of this, design of our landscapes may be
or prioritization. Unless regulated, often times the
particularly influential to holistic health. A goal of
breadth of health impacts go uncalculated due to
health can only be reached with a clear definition,
lack of funding or concern. Even if regulated, health
specific to local needs, in order to maximize
brackets are often set to minimal lawful standards,
health outcomes. Health should be defined by all
responding to population and statistical health, and
stakeholders in a project, including the surrounding
not necessarily neighborhood or individual health
community, stakeholders, the client, operations and
needs.
The potentials for improving industrially-modified sites and public health are great.
Many post
industrial sites lie along urban waterfronts, hogging prime real estate. As our cities continue to expand we are running out of land, and post industrial sites may provide inspiring opportunities for urban infill, particularly with creating publicly accessible waterfronts.
staff, and supported by applicable laws, policies or regulations.
08
Gas Works Park in Seattle is an example of how a redesigned post industrial landscape along the waterfront can improve health. [Friends of Gas Works Park]
Industrially-modified sites, such as these found in downtown Cleveland, can be very damaging to holistic health 09
[Leann Andrews]
SUB-HEADER
HEALTH AS THE GOAL
Landscapes Can Improve Health
Health As the Goal of Designed Landscapes Health was the motivating factor in much of nineteenth-century urban design.
Frederick Law
Olmsted, one of two designers of Central Park in NYC and a pioneer of the field of landscape architecture, held a dual life as a public health advisor on the U.S. Sanitary Commission. His designs, as well as the
or miasma, was produced by particular landforms,
While the miasmatic theory may have dwindled
therefore reducing discrimination and gangs, and
over the years, there are still niche sectors of the
providing a valuable outdoor space in a dense city to
landscape profession that focus on designing with
be used for human reflection, retreat and restoration
health as the goal.
(Szcaygiel & Hewitt, 1974). Even today, Central Park
and therapeutic landscapes are all designed with
is a landscape icon of the city and a source of pride
the idea that the landscape has the capacity to heal.
amongst New Yorkers. It is a peaceful yet stimulating
While stories of therapeutic horticulture is sprinkled
oasis nestled inside a bustling metropolis, and one
all throughout history, healing gardens regained
cannot help but feel the goal of health in its memory.
momentum in the 1990s, with research on their
Healing gardens, memorials,
effects published by the Kaplans (i.e. Kaplan, Kaplan
works of other designers of the time, responded to emerging medical theories that disease-laden air,
and community pride, integrating social classes and
Frederick Law Olmsted led a dual life as a landscape architect and public health advisor. [New York Public Library]
climates, and animal waste and was the source of epidemic disease that swept across the landscape (Szcaygiel & Hewitt, 1974). Olmsted designed Central Park with the idea that the reverse was also possible- that landscapes could be crafted to reduce miasma and therefore increase health. Olmsted envisioned Central Park as a public health amenity that would provide an escape from unhealthy urban stresses, purifying air and water, improving sanitation, increasing mental wellbeing
This idea that “unhealth” emerges from the
+ Ryan, 1998), Roger Ulrich (i.e. Ulrich, 1986),
landscape is referred to as the miasmatic theory, and
and other environmental psychologists. A special
was practiced from about 1840 to the 1890s. While
feature section on healing gardens in the Landscape
the miasmatic theory was adopted as common
Architecture
practice by sanitarians and planners, it was largely
(Dannenmaier, 1995) and a popular book by Clare
discredited by the medical profession who had
Cooper Marcus and Marni Barnes offering healing
rechanneled the blame of disease towards the newly
garden design recommendations (Marcus & Barnes,
discovered microorganism. With these technological
1999) furthered the popularity. As a result, many of
breakthroughs in the highly respected and influential
today’s hospitals, veterans centers, nursing homes,
medical profession, the miasmatic theory faded with
and outpatient treatment facilities have incorporated
the turn of the century and the close correlation
healing gardens into their campus designs, with the
between landscapes and health followed suit (Tesh,
goal that these designed landscapes might quicken
1995).
recuperation time, reduce stress, and improve
Magazine
by
Molly
Dannenmaier
mental health and well-being.
10
11 Central Park in New York City was designed with health as the goal. [personaltoursny.com]
Design for the World Trade Center Ground Zero Memorial [Michael Arad, Peter Walker]
Health As a Goal In Natural Landscapes
decreased local temperature
In recent years, much attention has been directed towards
understanding
capabilities of nature.
the
natural
healing
improve air quality
outdoor recreation
carbon sequestration
Because of this interest,
new interdisciplinary fields have emerged, such as ecopsychology which examines the psychological, spiritual and therapeutic aspects of human-nature relationships (Doherty, 2010) and nature therapy or
habitat creation
place of reflection
ecotherapy which seeks to use human exposure to nature as a viable treatment strategy for mental, physical and behavioral health problems (Wolsko &
neighborhood amenity
Hoyt, 2012). These emerging fields have developed a lexicon to communicate with newfound precision the relationship between humans and their natural
healthy child development
surroundings. Terminologies such as biophilia, the instinctive bond between human beings and natural systems (Wilson, 1984), and nature deficit disorder, describing the human costs of alienation from nature (Louv, 2009) have emerged to communicate this breadth of research on humans and nature.
stormwater infiltration flood reduction
sensory stimulation
increased property values
With rapid urban expansion and sprawl threatening
Novelist Richard Louv has taken this research one
our natural landscapes, increased leisure time
step further, and hypothesized the negative health
spent in the digital and televised world, and
effects on children not being engaged with nature,
decreased funding in school systems for outdoor
a term he coined nature-deficit disorder (Louv,
education, researchers have taken an interest in
2005). Later Louv expands this concept to argue
understanding the benefits of nature to influence
that a strong connection to nature is essential for
policy and protection of natural landscapes. The
all human health, boosting mental acuity, building
Human Environment Research Laboratory (HERL)
smarter economies, and strengthening human
at the University of Illinois, directed by researchers
bonds (Louv, 2011).
Frances Kuo, William Sullivan and later Andrea Faber
director of the Human Interaction with Nature and
Taylor, has firmly established a relationship between
Technological Systems (HINTS) Lab at the University
the presence of nature and greenspace to stronger,
of Washington, has explored how degradation of
safer, and healthier communities and individuals.
nature and modern technological and societal
The HERL has discovered that nature may increase
advances has affected human experience (Kahn,
a sense of community (Sullivan, Kuo & DePooter,
2011) and child development (Kahn, 1999).
2004), strengthen neighborhood social ties (Coley,
combined influence of these literary findings have
Kuo & Sullivan, 1997), decrease crime and fear
led to the formation of the No Child Left Inside
(Kuo & Sullivan 2001) and may promote healthy
Coalition, and legislative movements
child development (Taylor & Kuo, 2006). The HERL,
the No Child Left inside Act of 2008 and 2009,
which later became the Landscape and Human
advocating for funding and curriculum changes to
Health Laboratory, has discovered that children
include environmental education in school systems
with Attention Deficit Hyperactivity Disorder (ADHD)
(Benbow & Camphire, 2008).
Additionally, Peter Kahn,
The
proposing
have reduced symptoms when engaged with nature (Faber & Kuo, 2009 and Kuo + Taylor, 2004).
12
13
Bridal Veil Falls, WA [Leann Andrews]
Harnessing Health In Natural Landscapes To Apply To Designed Landscapes With over 50% of the world population living in cities (United Nations, 2007), urban areas are expanding at a rapid rate, consuming natural resources and transforming the texture of urban and suburban areas to that of concrete, brick and asphalt. Urban planners around the world are developing conservation plans and greenspace visions for their cities to preserve what little natural ecosystems are remaining.
This attention towards urban ecology
paralleled with the onset of the ‘green’ sustainability movement in the past decade has researchers and designers addressing the human benefits of designed nature in their work. The term green infrastructure is often used to describe the layers or systems of designed nature that have widespread environmental and public health benefits. Green infrastructure includes design interventions such as street trees, wetlands, daylighted streams,
services, have inspired studies that examine the
urban forests, bioswales, raingardens, green roofs
effect designed nature has on improving air quality
and walls, and even simulated nature such as
(Currie & Bass, 2008 and Buccolieri et al., 2009),
permeable pavement (Rottle & Maryman, 2012).
thermal regulation (Bass, 2007 and Mackey, Lee &
The incorporation of green infrastructure into the
Smith, 2012), economic health (American Rivers et
landscape architecture and planning professions
al., 2012, Thurston, 2012 and Wolf, 2007), social
has sparked a new design interest, ecological design.
health (Peters, Elands & Buijs, 2010 and Sullivan,
Ecological design aims to improve upon biological
Kuo & DePooter, 2004), safety (Macdonald, 2008
integrity by proposing design interventions that
and Johnson, 2008) and academic and workplace
address human needs while supporting the health of
performance (Matsuoka, 2010 and Kaplan, 1993).
natural systems (Rottle & Yocom, 2011). Additionally,
When viewed at a much larger scale, designed nature
research areas such as phytoremediation, the use
in our cities could reduce the harmful health impacts
of plants to remove contaminants (Arthur et al.,
of climate changing conditions (Frumkin, 2011).
2005), and mycoremediation, the use of fungi to do the same (Stamets, 2005) have grown exponentially in the past few years, discovering further ways to
Conclusion: Landscapes Can Improve Health
employ nature to improve human health. Reacting to the popularity of Leadership in Energy
In sum, both the natural landscapes and the
and Environmental Design (LEED) certification, and
incorporation of nature and natural systems in
the Sustainable Sites Initiative (SITES), designers
the designed landscape are uniquely capable of
are looking to harness the health benefits of
providing multiple human health benefits. Through
natural landscapes to incorporate into designed
the strategic incorporation of designed nature and
landscapes, and communicate those results to their clients.
the preservation of naturally occurring landscapes,
These benefits, referred to as ecosystem
14
our landscapes have the capacity to heal. Living wall on Qui Branley Museum, Paris [Gilles ClĂŠment and Patrick Blanc]
15
Tanner Springs Park, Portland OR [Leann Andrews]
The Built Environment and Health
The Built Environment Can Affect Health Most people spend virtually every minute of every day moving through different aspects of the built environment.
The built environment consists of
our surroundings that are designed, created and maintained by humans and includes buildings, neighborhoods,
plazas,
playgrounds,
roadways,
parks, and their supporting infrastructure.
In
their book, Making Healthy Places, editors Andrew Dannenberg, Howard Frumkin and Richard Jackson discuss how the built environment profoundly affects physical, mental, social, environmental and economic health and wellbeing (2011).
Although
often overlooked in medical practices because of its difficulty to assess, the built environment can heavily influence human behavior, daily choices, and life opportunities that may lead to healthy or unhealthy living. Because of its enormous influence on human lives, a mindfully, healthfully designed, planned and operated built environment could even act as a form of widespread preventive medicine for unhealth
16
of all forms, halting some diseases, illnesses and
such as safe crosswalks or pedestrian/vehicular
Conversely, the built environment can also have
disabilities long before they even come to fruition
buffers (Sleet, Naumann & Rudd, 2011). The design
powerful negative health consequences, especially
(Frumkin, 2011).
of the built environment can impact how storm and
for vulnerable populations, such as those with
wastewater flows throughout a community and how
underserved attributes (i.e. age and disability) and
The built environment can positively affect the way
pollutants impact critical ecosystems and the food
social constructs (i.e. race, ethnicity and poverty).
we lead our lives. For example, the built environment
we consume. By designing our communities with
Environmental exposures such as unsafe housing,
can influence how much physical activity we have
the proper infrastructure to reduce mold, flooding,
incomplete transportation systems, or inaccessible
the opportunity to engage in, and therefore prevent
and exposure to fecal matter, we can reduce air and
buildings
numerous physical and mental health conditions.
waterborne diseases, and ecological degradation
specifically for those who do not have the economic
The inclusion of bike trails, sidewalks, and parks in
(Backer, 2011). Public spaces, community centers
or social structures to offer alternative opportunities
neighborhoods provides for more opportunities to
and parks may draw people together and thus
(Kochtitzky, 2011). Noisy, crowded and dangerous
exercise than those that lack these amenities (Sallis,
support the development of social ties and enhance
places may have negative mental and psychological
Millstein & Carlson, 2011). Access to healthy food
the development of
social capital, supporting
health impacts such as stress, anxiety disorders,
options such as grocery stores, farmers markets,
mental health and well-being (Eicher & Kawachi,
depression, and even violent behavior (Sullivan &
and community gardens in our neighborhoods may
2011). Schools, hospitals, workplaces, homes and
Chang, 2011). Lastly, the strength and redundancy
provide for healthier food choices, shrinking our
other buildings can all be designed with proper
of ecological and man-made infrastructure present
body masses and the probability of getting diabetes
air circulation, temperature, sunlight and without
in a community may play a large part in the
(Cannuscio & Glanz, 2011). Reducing air pollution
exposure to chemicals to positively influence how our
resiliency to natural disasters.
through carefully designed roadways and alternative
bodies can cope with mental and physical illnesses.
neighborhoods with poor preparedness planning,
may
create
adverse
health
affects,
Disasters that hit
transportation options may reduce the effects of
ecological and building design, and weak social
asthma and the risk for lung or other chronic diseases
networks may damage the community past the point
(Samet, 2011). Injuries, one of the major causes of
of recovery (Beatley, 2011).
death, may be prevented through modifications of the environment to reduce risk and increase safety,
17 Singapore’s EDITT Tower uses the built environment to rehabilitate a damaged urban landscape and promote health and wellbeing. [T R Hamzah & Yeang]
The Built Environment Can Be Toxic While many aspects of
the built environment
heavily influence healthful human behavior, choices, and opportunities, a few aspects of the built environment are dramatically damaging to human health. Two such examples of toxic aspects of the built environment are below. In the late 19th and early 20th centuries, cities in the United States laid down public infrastructure to solve major health problems such as disease epidemics caused by on-site waste. To save cost and building materials, many cities built combined sewer systems, single pipes that handle both sewage and urban runoff from streets and roofs.
The infrastructure
planners and engineers at the time over designed these system to capture three to five times the average dry weather flows, however rapid urban expansion and an increase in urban density and impermeable surfaces has caused these systems to carry loads that exceed the maximum limits of wastewater treatment plants, discharging untreated
storm and wastewater, or combined sewer overflows
underutilized industrial and commercial facilities,
(CSOs) to nearby rivers, streams and lakes (United
are often contaminated with toxins left over from prior
States, 2004). The pollution caused by CSOs has
industrial use (U.S. EPA, 2006). Those brownfields
destroyed many aquatic ecosystems, decreasing fish
that are particularly hazardous to human health
consumption and markets, and causing many public
are placed in the prioritized Superfund program,
waters and beaches to be unsanitary for public use.
a cleanup fund established by the Comprehensive Environmental
Response,
Compensation
and
Around the same time, the industrial boom of the
Liability Act (CERCLA) of 1980 (U.S. EPA, 2012a).
early 1900’s created great economic opportunities.
The Superfund cleanup program was established
The urban landscape was dotted with thriving
in response to the environmental tragedy of Love
factories,
refineries
and
worker
housing
and
industrial transportation systems were flourishing.
850 billion gallons of untreated sewage enters our waters nationwide from CSOs. [StokeReport.com]
Canal, where hazardous waste leaching from a buried industrial landfill was suspected to be the
Today, American cities have undergone a dramatic
cause of numerous cancers, birth defects, chronic
spatial transformation. With de-industrialization,
illnesses and deaths (Beck, 1979).
urban sprawl, 9/11 recovery and the mortgage housing crisis, cities are experiencing incinerating
Over 770 U.S. cities spew 850 billion gallons of
holes in their urban fabric. These abandoned land
untreated sewage each year due to combined sewers
scraps are cultural graveyards, toxic urban waste,
overflows (US EPA, 2012c).
and breeding grounds for crime.
The rustbelt in
Superfund sites, 1,000 of which are on the National
particular, extending from Chicago to Pittsburgh
Priority list, (US EPA, 2012b) and an estimated
and swinging up to Buffalo, has been in continual
450,000 brownfields across the country (US EPA,
economic decline over the past 30 years due to
2011). These toxic aspects of the built environment
globalization of the steel and automotive industries
may have serious consequences to human and
(“Rustbelt”, 2003).
Brownfields, abandoned or
18
environmental health.
Abandoned brick factory in my hometown, South Beaver Twp, PA. [Leann Andrews]
There are 40,000
EPA Superfund Site Status Map, March 2010, displaying the 40,000 toxic Superfund sites sprinkled throughout the country. [US EPA]
19
Evaluating And Applying Health To The Built Environment In the healthcare industry, the growing practice of Evidence-Based Design is based on the understanding that healthcare buildings play a key part in health outcomes.
Evidence Based Design (EBD) is
described as “the process of basing decisions about the built environment on credible research to achieve the best possible outcomes” (The Center for Health Design, 2008). By linking design decisions to key performance outcomes that have been systematically and professionally assessed, the architect can maximize building function, and therefore health outcomes (Harris et al., 2008). EBD ideas are closely linked to the growing practice of Evidence Based Medicine, or the systematic process of evaluating scientific research that is used as the basis for clinical treatment choices (Claridge & Fabian, 2005). Very similar to the practice of law, Evidence Based Medicine looks at precedent studies and results to diagnose and treat current patients.
Although it can be applied to all types of design, EBD
design profession (Francis, 2001). In their book,
and policies.
HIAs pair science with professional
is rarely practiced outside the design of hospitals
Design Informed: Driving Innovation with Evidence-
experience to visualize the best possible health
and other medical facilities. Design professionals
Based Design, Robert Brandt, Gordon Chong, and
outcomes for a project or policy. While HIAs can
typically depend on intuition and personal project
Mike Martin argue that EBD is the best way to
yield valuable recommendations to maximize health
experience to make design choices. However, with
achieve design excellence, and could radically shape
outcomes in the built environment, they can be quite
advancements in modeling software, an increased
the architecture of the future (2010). Although it
costly and, because they are voluntary in the United
interest in LEED and sustainability projects, paired
shows much promise, the use of EBD by designers,
States, financial interests and other political factors
The built environment we experience in our daily lives
with hard budgetary times, a form of EBD is beginning
and even more specifically landscape architects,
may stand in the way of recommendations being
greatly affects the health of people. landscapes, and
to be used as a tool for designers to justify costs to
has largely been untouched outside the hospital
carried out in built environment design (Dannenberg
ecologies. It influences our exposure to harmful toxins
their clients (Brandt, Chong, & Martin, 2010). For
industries.
et al., 2008).
and chemicals, our mental wellbeing and perception
within their design, model how long it will take for
While not as readily utilized in the design industry,
Emerging trends of evidence-based practices in
them to pay for themselves and the amount of
the public health and planning industries are leading
medicine, healthcare facility design, sustainability
carbon saved, and look at examples of other studies
the evidence-based initiative in the built environment.
projects, and public health and planning may
Understanding this great influence that the built
that have documented the savings by solar energy.
Evidence-Based
identify a need for landscape designers to adopt
environment has on health may lead to more healthful
Additionally, the Landscape Architecture Foundation
incorporation of scientific evidence in selecting and
similar practices.
design, planning and policy-making.
(LAF) has recently started a collection of case
implementing large-scale programs and policies, is
design directly and indirectly affects health may
based design techniques may help communicate
studies on actual landscape performance, which
being fueled by public concerns that intervention
also identify a need for health to be more closely
health outcomes, while stimulating further research
in the future may be used by design professionals
decisions are often based on perceived short-term
incorporated into design practices. While designers
studies and educating those in the built environment
as “evidence” (Landscape Architecture Foundation,
opportunities at a high societal cost and a low health
are not currently trained to understand health
professions of the potentials they have to influence
2011). While the current definition of EBD relies
return (Baker et al., 2011).
Tools such as a Health
consequences of their design decisions, an increased
widespread public health improvement.
on published and peer-reviewed scientific research,
Impact Assessment (HIA) are beginning to be used
understanding of health outcomes may be critical to
these techniques of software modeling and case
by planners and public health officials to assess
creating healthier communities and lives.
studies may be better suited as evidence in the
the potential health outcomes of proposed projects
example, a designer might incorporate solar panels
20
Conclusion: Smart Design of the Built Environment May Positively Affect Health
of the world, and impacts human behavior, choices
Public
Health
(EBPH),
or
the
Recent understanding of how
and opportunities that affect health.
Evidence-
21 City Farm has a goal to transform all 80,000 vacant lots in Chicago into urban farms, improving the health of the community and landscape. [Letitia L. Star]
Urgency and Interest
OBESITY EPIDEMIC [CDC] In recent years, health issues in the United States have grown exponentially, grabbing the attention of the media as well as political, economic, and research professionals. Rapidly increasing mental and physical illnesses and an increased burden of healthcare costs severely degrade life satisfaction as well as social and individual wellbeing. While the United States is the 7th wealthiest country in the world (Greenfield, 2012), it only ranks 25th in the World Values Survey and the European Values Survey on happiness and life satisfaction (Pappas, 2012). Climate changing conditions will further exacerbate health issues, with increased intensity in weather and natural disasters as well as an upward creep in tropical diseases (Frumkin, 2011). Furthermore, with 12.5 million (8.1%) unemployed in (U.S. Dept. of Labor, 2012) and a staggering 49.9 million (16.3%) uninsured (U.S. Dept. of Health and Human Services, 2011), health may become an indicator of wealth and power. The health situation in the United States is reaching crisis levels, and healthcare professionals are beginning to look “upstream” to built environment disciplines to prevent disease and improve quality of life for all Americans (Jackson,
Health Realities of Today Nearly half of Americans are living with a chronic condition (Partnership for Solutions, 2004) and a staggering $2.3 trillion is spent on medical costs each year (Orszag and Ellis 2007).
For the first
time in American history, if health trends are not reversed, today’s youth could be the first generation to have a shorter average life span than their parents (Olshansky et al, 2005). The obesity epidemic among people of all ages is astonishing.
The percentage of Americans that
are overweight or obese has risen from 45% in the 1960s to a staggering 67% today (CDC, National Center for Health Statistics, 2009 and Flegal 2010). In 1985 no state reported an obesity rate higher than 15%, compared to today where every state except Colorado has an obesity rate greater than 20% (CDC 2010).
CDC reports a shocking 1/5
of American children are clinically obese, which is four times the amount reported in the late 1960s (Lumeng, 2005). Obesity has been known to lead
to increased risk for diabetes, heart disease, stroke,
across the world; i.e. United Nations Conference on
high blood pressure, cancer, joint and bone disease,
Happiness 2012 (Helliwell, Layard & Sachs, 2012),
depression, birth defects and other serious health
Gallup-Healthways Well-Being Index (Gallup, 2012b),
problems (Dannenberg, Frumkin, & Jackson, 2011).
World Values Survey (World Values Survey, 2012), European Values Study (European Values Study,
Mental health and wellbeing is also a growing
2012), The National Happiness Initiative (Happiness
concern. The percentage of the population receiving
Initiative, 2012), Gross National Happiness USA
antidepressants has doubled since the mid-1990s,
2012 Conference (GNH USA, 2012), the NEF Happy
making them the most prescribed medication in
Planet Index (NEF, 2012), and the World Database
the United States (Olfson and Marcus, 2009). The
of Happiness (Veenhoven, 2012).
rate at which American children are prescribed antidepressants almost doubled from 1998-2003,
Our natural resources are being depleted at an
of which the steepest increase (66%) was among
alarming rate.
preschool children (Delate et al., 2004).
Monthly
wetlands were lost at a rate of over 60 acres/
reports on happiness on wellbeing in the United
hour. At the time of Colonial America there were
States report that in the Month of April 2012,
an estimated 392 million acres of wetlands (Dahl,
42.9% of people are “struggling”, with an overall
1990), compared to today where less than 27%
“happiness score” of only 49% (Gallup, 2012a).
remain (Zinn & Copeland, 2001). In the last decade
In Seattle, growing concern for human wellbeing
in the U.S., an average of 6,000 acres of forest and
in their city led to the creation of the Seattle Area
natural open space has been lost per day, or an
Happiness Initiative and the Seattle Happiness
area about the size of Seattle every 9 days (USDA
Report Card (SAHI, 2011).
Recent worldwide
Forest Service, 2007). Riparian habitats are being
reports and conferences on happiness levels express
replaced with urban edges and our water quality
a growing concern for the state of human wellbeing
is being severely degraded by toxins from human
Between the 1780s and 1980s,
2011). 22
23
Because of today’s widespread public health issues, such as the obesity epidemic, healthcare professionals are beginning to look “upstream” for solutions in the built environment disciplines.
life. With increased urbanization and urban sprawl,
Nations, 2011) we are losing our experiences with
farsighted. Using a computer for 9+ hours a day
healthcare. Almost 50 years later, the proportion
natural landscapes that do remain are fragmented
natural areas, and maybe becoming a more stressed
is extremely straining on the eyes and is linked to
had increased to 16% of GDP (Orszag and Ellis
and of low quality, resulting in low biodiversity and
population.
Computer Vision Syndrome (Blehm et al., 2005)
2007). With the aging baby-boomers, the proportion
and potentially glaucoma (Meikle, 2004). Over the
of Americans over the age of 65 is expected to
ecosystem function.
This habitat destruction has
both direct and indirect health consequences. Trees
With depleting nature in our urban, and non-urban
last generation, hearing loss has increased at a rate
increase from 12% in 2009 to nearly 20% in 2030,
assist in carbon sequestration and air purification,
areas, we as a species are relying on artificial
of 160% in America, affecting about 11% of the
inevitably projecting an even further increase in
a significant loss when being replaced by roads
and digital nature to fulfill our human needs.
population (Kochkin, 2009).
medical costs (Administration on Aging, 2010)
and buildings, where more than a third of air
With more and more of our lives spent watching
pollution comes from our transportation systems,
television, staring at computer screens, and sitting
Additionally, our urban areas are ticking time
chronic diseases are also increasing. An estimated
and more than half from energy use in buildings
in air conditioning, our senses are becoming more
bombs, leaking industrial toxins in the air and water
49.9 million people (16.3%) are uninsured (U.S.
(Dannenberg, Frumkin & Jackson, 2011). Natural
and more two dimensional. Richard Louv, an
at a faster rate than our current cleanup efforts can
Dept. of Health and Human Services, 2011) and an
habitat regulates temperatures and reduces the
environmental novelist, notes, “today the life of
afford. With over 450,000 brownfields (US EPA,
even larger number has inadequate insurance and
urban heat island effect, the phenomena where
the senses, is, literally, electrified” (Louv, 2005).
2011), 1,000 of which are on the National Priority
cannot afford the health services they need.
cities are actually warmer than their surroundings.
Professor Robin Moore at North Carolina University’s
List for known human health hazards (US EPA,
Nature not only regulates local climates, but also
National Learning Initiative, explains that multi-
2012b), we need to find more efficient and affordable
the global climate.
Rapid degradation of natural
sensory experiences in nature matter because they
cleanup practices. In many cities, the prime urban
systems is associated with acceleration of climate
help build “the cognitive constructs necessary for
waterfront real estate is being consumed by these
changing conditions, causing an increased intensity
sustained intellectual development”, stimulating
toxic abandoned sites, and with cities doing their
in weather damage, injuries and diseases (Frumkin,
imagination and wonder that we carry with us
best to reduce sprawl, they are running out of
2011). From a mental wellbeing perspective, there
from childhood into adulthood. Furthermore, even
uncontaminated land to build on.
are over 100 studies that confirm that spending time
our over utilized dual senses are taking a toll. The
in nature reduces stress (Kahn, 1999). With nearly
Vision Council of America estimates that 75% of
Lastly, medical costs have increased exponentially
83% of the nation (UNICEF, 2012) and 3.5 billion
adults use some sort of vision correction agent (i.e.
over the years. In 1960, the United States was
people in the world living in urban areas (United
glasses or contacts) and 60% of Americans are
spending 5% of the Gross Domestic Product on
24
Although our medical spending increases, rates of
Urban sprawl is depleting our natural resources, replacing human experiences with nature with urban stress [top: NASA, NOAA “night lights” bottom: Clark Cty, NV, Christoph Gielen, NY Times]
25
The 450,000 brownfields and 1,000 Superfund sites are ticking time bombs, leaking dangerous toxins into our environment and degrading human health. [top: Elisabeth Copper Mine Superfund Site, Vermont, USGS bottom: Lower Duwamish River Superfund Site in South Seattle, WA Dept of Ecology]
Renewed Interest In The Built Environment To Address Health Because of these seemingly overwhelming health issues in our current society, health professionals are looking outside their profession to examine root causes. This has led to a renewed interest in looking at the built environment as a way to address health, as a form of preventive medicine (Frumkin, 2011). More importantly, this renewed interest is coming from both ends- from planners, landscape architects, architects, public health officials, doctors, and researchers in both the built environment and health professions. This excitement can be seen in books, journal and magazine articles, news clippings, exhibitions, and conferences. A brief window into the magnitude of this interest: Selected books published in the past 3 years:
Building American Public Health: Urban Planning, Architecture and the Quest for Better Health in the United States (2012) Imperfect Health: The Medicalization of Architecture (2012) Making Healthy Places: Designing and Building for Health, Well-Being and Sustainability (2011) Designing Healthy Communities (2011) An Introduction to Community Health, Seventh Edition (2011) Changing Planet, Changing Health: How the Climate Crisis Threatens Our Health and What We Can Do about It (2011) The Agile City: Building Well-being and Wealth in an Era of Climate Change (2011) The Nature Principle: Human Restoration and the End of Nature-Deficit Disorder (2011) Sustainable Environmental Design in Architecture: Impacts on Health (2011) Improving Health in the United States: The Role of Health Impact Assessment (2011) Toward the Healthy City: People, Places and the Politics of Urban Planning (2009) Thriving Beyond Sustainability: Pathways to a Resilient Society (2010) Living Downstream: An Ecologist’s Personal Investigation of Cancer and the Environment (2010) Urban Health: Readings in the Social, Built and Physical Environments of U.S. Cities (2008) Cities for People (2010) Innovative Approaches to Researching Landscape and Health (2010) Biophilic Cities: Integrating Nature into Urban Design and Planning (2010) Healing Spaces: The Science of Place and Well-Being (2010) Pedaling Revolution: How Cyclists are Changing American Cities (2009) Shopping Our Way to Safety: How We Changed from Protecting the Environment to Protecting Ourselves (2009) Biophilic Design: The Theory, Science and Practice of Bringing Buildings to Life (2008) Therapeutic Landscapes: Geographies of Health (2008) Health, Sustainability and the Built Environment (2008)
Selected Conferences and Symposiums scheduled for 2012: SAR Architecture for Health Spring Conference, Clemson, SC Center for Health Design’s Healthcare Design Conference, Phoenix, AZ Urban Systems Conference: Urban Change- Education, Health and the Environment, Rutgers-Newark, NJ Making Cities Livable Conference: True Urbanism- Planning Healthy Communities for all, Portland, OR Healthcare Experience Design Conference, Boston, MA 1st National Health Impact Assessment Meeting, Washington D.C. International Conference on Landscape and Health, Zurich, Switzerland International Academy of Design and Health 8th World Congress and Exhibition, Kuala Lumpur, Malaysia 3rd Design + Health Australasia International Symposium, Sydney, Australia 2nd International Symposium on Design and Health Europe, Helsinki 2nd Design and Health Africa Symposium, Johannesburg 2nd Annual Landscape and Health Conference: Effects, Potentials and Strategies, Birmensdorf, Switzerland The 7th International Conference on Persuasive Technology: Design for Health and Safety, Linkoping, Sweden
Daylighting, Architecture and Health: Building Design Strategies (2008)
26
27
Percentage Increase in Health Insurance Premiums Compared to Inflation, 2000 - 2009 Landscape architects will need to
in our food and environment, growing population,
start speaking up if they wish to bring their skills to
economic recession and attention to purposeful
the table and tap into a blossoming market.
and practical living, and a desire to live longer, happier and more beautiful lives are contributing to a cultural push that may swing the interest of
Estimated Deaths Attributed to Climate Change in the Year 2000, by Subregion*
Richard Jackson, co-editor of the book Making
professionals into mainstream media. Just as the
Healthy Places, writes:
word ‘sustainability’ has transformed the way we all look at the environment, the work ‘health’ may
“The modern America of obesity, inactivity, depression
create just as powerful of a revolution. Designers,
and loss of community has not ‘happened’ to us; rather
in particular, are motivated by buzzwords, and there
we legislated, subsidized, and planned it.”
just may be a life-changing market for the word ‘health’. While
there
publications
Conclusion: An Urgency and Interest in Health May Open Doors for Designers, and Landscape Architects in Particular
If this is in fact true, that we are directly responsible are and
numerous conferences
books,
for our pressing health issues of today, then there
articles,
surrounding
must be a way to legislate, subsidize, plan, and I would
the
add, design ourselves out of this unhealthy mess.
topic of health and the built environment, the
By 2040 the majority of buildings in America would
dialogue between landscape architects and health
have been designed and built with the knowledge of
professionals is not as strong as it is with other built
LEED standards and the decline of the rustbelt, (and
environment professionals. Only one of the books in the previous pages was written by a landscape architect, compared to the 6 written by architects, and 5 by planners. The reach from public health is even stronger, with 8 books coming from health
sustainability as a goal, and to dramatically improve the health of our current and future landscapes, ecologies and people. The urgency and interest in health may open new market opportunities for landscape architects and other design professionals.
Urgency
professionals.
Design, framed as
preventive medicine, may be a solution to addressing the increasingly overwhelming health issues we face in today’s society. nature,
[Keiser/HRET Survey of Employer-Sponsored Health Benefits, 1999-2009. Bureau of Labor Statistics, Consumer Price Index, U.S. City Average Inflation (April to April), 1999-2009.]
Because of their collaborative
systems-oriented
thinking,
multi-scale
experience, and holistic design approach, landscape
Number of Stories in News Coverage, 2005-2010
architects may be particularly situated to address these multifaceted health issues. The conversation is gaining momentum, however, and landscape architects will need to join the dialogue soon or their skills will be overlooked and replaced by other design professionals such as architects, engineers, and planners.
Interest
The climate change scare, attention to chemicals
consequently the birth of the brownfield), would [Data: McMichael, JJ., Campbell-Lendrum D., Kovacs RS, et al. Global Climate Change. In Comparative Quantification of Health Risks: Global and Regional Burden of Disease due to Selected Major Risk Factors. M. Ezzati, Lopez, AD, Rodgers A, Murray CJL. Geneva, World Health Organization, 2004. Map: Center for Sustainability and the Global Environment (SAGE) ] The health issues that surround climate changing conditions may lead to an urgent need for smarter and more healthful design.
have happened more than 70 years ago. With our current knowledge, technology, and interdisciplinary interest, there is really no excuse not to design with [HfS Research/Google, 2011]
28
29
The urgent health conditions of today and a renewed interest in health in design, may open a preventive health market for landscape architects and other design professionals.
Conclusion
A New Approach to Contemporary Design: Health as the Goal In sum, design, and particularly landscapes, have the capacity to affect health; however designers may not be fully aware of the extent their design decisions could have. These findings may identify a need for:
•
Health to be (re)established as the goal of landscape design
•
An increased understanding of health outcomes by designers
•
A potential need for modified evidence-based research and practices in landscape design
•
More
interdisciplinary
collaboration
and
innovation in design to address the growing health concerns
•
More
input
from
landscape
architects
in
particular, on health and the built environment issues and solutions
While this crossover of professions is becoming an process
emerging interest on both ends, there are very few
may create more salubrious results, however the
professionals who are dually educated. Currently a
integration will not be simple.
Communication
niche health-design profession does not exist outside
channels between health and design professionals
research and academia. There is promise, however,
may be difficult to overcome.
with schools such as the University of Washington
Incorporating
health
into
the
design
Buzz words and
technical vocabulary have evolved separately and
offering
without much influence over the years, creating
classes that are well received, and educators in both
language
the built environment and health disciplines seeking
barriers.
Landscape
design
and
optional
interdisciplinary
health-design
health professions often have different training
out dual-associate professorships.
Furthermore,
philosophies that develop different professional
design studios at the University of Washington are
brains. Landscape architects are trained to examine
centered around exploring health and wellbeing
systems and patterns first, then funnel down to
issues, beginning the integration of health in the
details, with results considered last. They are taught
design process for the next generation of designers.
to embrace natural processes and understand that time and the environment are unpredictable factors in the equation. Health professionals, however, think oppositely, looking at diagnostic details and results and then projecting out to larger patterns and systems. Because of the seriousness of the topic, health aims for accurate prediction and control of results.
30
31
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37
A FRAMEWORK TO INCREASE UNDERSTANDING
HEALTH IN DESIGN
01
A FRAMEWORK TO INCREASE UNDERSTANDING
HEALTH IN DESIGN
Introduction
Health in Design The built environment can have a great affect on health. In order to maximize its healthful potential, the designers responsible for shaping the built “To know that even one life has breathed easier
environment must be aware of the correlation
because you have lived, that is to have succeeded.”
between health and design and the consequences of their design interventions. Common contemporary
— Ralph Waldo Emerson
design practices do not consider health in the design process, if at all, and this lack of dialogue may reduce health potentials or even create unhealthful results.
A framework for viewing health in
design may result in an increased understanding of health outcomes for designers, clients and the general public about how the built environment affects individual and community health.
With
this framework, a new profession may emerge to become the bridge between the health and design worlds. This framework may become a tool to guide deisgners and clients to achieve more salubrious results, and could even disappear over time when the
How might a health conversation be incorporated into the design process to increase understanding of consequences of design?
health conversation becomes more commonplace.
This section explores how health can begin to enter into the design conversation.
construction.
By incorporating
education within the design process, designers can begin to understand both the negative and positive consequences of their design actions. This increased understanding may bring to light the large impact that designers have on the health of individuals
Likewise, the health-design profession may fade over time, if health enters into everyday design dialogue. The following pages explore the capacity for a framework to increase understanding of health, using DIG Studio’s project as a test example of the framework process. This section asks the question:
and the communities they live in. Education while inside the design process may help inform design thinking, and allow for changes to happen before
02
03
the health
Health Dialogue
Define Health Through the Goals of the Project
Need for a 3rd Party Health Champion
those without a voice such as the disadvantaged
Health is personal, contextual and complex, making
Project Goals From Multiple Perspectives
it difficult to define, and therefore difficult to design with health as the goal. Because of this, in landscape design it is best to define health through the goals of the project involving the desires of all current and
of the stakeholders, but also be able to represent
community
design professionals
regulatory
client / operations
An issue with collecting goals from multiple
populations and the environment itself. The Health
perspectives lies in facilitating and translating with
Champion would be skilled in translating and
a genuinely open mind, and without bias towards the
communicating to all parties, mindful of jargon and
designer, client, or a particular user. Additionally,
professional perspectives, as well as financial and
very few people are skilled in understanding both
cultural realities and constraints of construction.
complex health issues as well as the creative design This
One aspect of this thesis explores the feasibility of
a regulatory standard. Existing conditions analysis
may identify a need for a third party mediation...
such a position. By walking through a health/design
performed by the designer, client and any regulatory
a Health Champion that would defend the health
process with a group of student designers working
definition and the needs and desires of all parties.
on their capstone project, this thesis explores the
future stakeholders, not just a designer’s vision or
agency involved will identify unhealth and issues with the current state of the site. Public meetings and outreach will collect the community perspective on issues and community vision. Careful attention
PARTICIPATORY PUBLIC MEETINGS + OUTREACH
EXISTING CONDITIONS ANALYSIS
AGENCY REPORTS + ANALYSIS
DESIGN MEETINGS
LAWS + POLICY
SITE LOCATION, FINANCING + OPERATIONS
process and the intricacies of construction.
following questions: The Health Champion could be one person or a neutral organization acting as a translator and
•
How can the Health Champion help designers
should be made to gather perspectives from all
communicator through the design, health, and
to understand the health implications of their
community
community worlds.
designs?
populations,
especially
those
with
Ideally, the Health Champion
softer voices. Initial design meetings with design
would be a designer who is knowledgeable in public
professionals and the client will translate community
health, policy, and regulatory requirements or visa
needs
and
desires
and
brainstorm
solutions.
Operations and site management view should also
3RD PARTY INTERPRETS // CONSOLIDATES // CATEGORIZES GOALS
versa. The Health Champion would be able to openly
•
How can understanding health make better design?
facilitate public meetings and participatory design
have input on the goals of the project. A definition
charettes as well as client and design meetings. The
The following pages outline the process of the Health
of health will emerge from identifying the goals of
Health Champion would not only speak on behalf
Champion walking the designers through a healthdesign framework to explore these questions.
the project. 04
05
Developing a Health Framework
Developing a Framework to Understand Health To explore the idea that an understanding of health can contribute to better design and more salubrious results, this thesis develops a design framework. The design team moves through the framework to make the connections between their design interventions and their effects on both individual and community health.
Health analysis and evaluation of design
happens within the design process, rather than after design completion or construction to influence outcomes at a low cost.
Moving the designers
through a health framework in the design process will help inform how they think about future design, with the framework potentially unnecessary over time.
of these framework strategies are the following:
Strategy 1: Design to Outcomes The initial framework tested a simple relationship between design ideas, the potential results of those designs, and the health outcomes of each.
The
resultants were grouped in categories of ecological, social and economic for ease in digestion.
The
outcomes looked at both individual health and wellness,
and
each
translated
to
community
revitalization. After running through the framework with the design team who were in their initial brainstorming stages of their project it became clear that beginning with design concepts was not helpful in informing more healthful design development decisions, but rather validated existing design ideas. Additionally,
Three different framework strategies were tested before a recommended framework was chosen. Each of the frameworks were tested on a team of students while in the beginning stages of the design
Framework Strategy 1 Design to Outcomes Pros: • straightforward and easy to add into current design process • designers began thinking about health
Framework Strategy 1: Design to Outcomes
DESIGN IDEAS DESIGN
POTENTIAL OUTCOMES HEALTH
SOCIAL ECONOMIC
Cons: • beginning with design doesn’t influence outcomes • more validation than education • categorization of resultants unhelpful and tedious • categorization of outcomes subjective and unhelpful • categorizations difficult since many spanned multiple categories • uninspiring, did not influence design or change outcomes
categorizing the resultants and outcomes was tedious, subjective, and unhelpful, since many spanned multiple categories and the grouping did not change the outcomes.
process for a capstone project. The results of each
06
POSSIBLE RESULTANTS ECOLOGICAL
07
WELLNESS
COMMUNITY REVITALIZATION
ATSDR Steps in Developing a Healthy Community
Strategy 2: Goals to Outcomes The next strategy was loosely based an existing tool
While a much more in-depth process, this framework
used in the Agency for Toxic Substances and Disease
was wildly unsuccessful.
Registry (ATSDR) out of the U.S. Department of
tested the framework could not move beyond
Health and Human Services.
identifying the goal criteria.
The ATSDR uses
Framework Strategy 2: Goals to Outcomes
The design team that ATSDR Community Health Evaluation
The failure was due
this tool (shown at the right) to inform residents
in part to the framework’s linear nature, inhibiting
near brownfields of public health concerns and
the natural design process. Design is much more
redevelopment opportunities (ATSDR, 2010).
organic and less mathematical. The design team
(Physical + Mental Health, Safety + Security, Housing, Education, Economy)
did appreciate considering goals of the project and This framework strategy digs further into the design
felt it was helpful in informing design decisions in
process by beginning with identifying goals of the
the future. This framework also revealed a need to
project and criteria needed to meet those goals.
group “health” and “wellness” together, since one
Design is then introduced and resultants and health
informs the other, and to begin to examine how one
outcomes are extrapolated.
would evaluate results.
Lastly, the outcomes
Framework Strategy 2 Goals to Outcomes
CRITERIA TO MEET GOALS
design has affected health.
08
[Agency for Toxic Substances and Disease Registry]
DEGREE OF OUTCOMES
Pros: • in-depth process • considering health from the beginning in goals • grouping health and wellness together • considering how one would evaluate results Cons: • too linear • inhibited creative design process • unnatural and painful for designers • uninspiring, did not influence design or change outcomes
are analyzed to determine the degree to which the
INDIVIDUAL HEALTH OUTCOMES
DESIGN SCRIPTS
PROJECT GOALS
09
DESIGN RESULTANTS
COMMUNITY HEALTH OUTCOMES
Strategy 3: Organic Flow The third strategy is flexible enough to allow for a freeflowing creative design process while also adding layers of information regarding health into design development. Instead of forcing designers to follow a health framework outside their training and comfort zone, the health dialogue is essentially embedded within the design process. The designer begins identifying issues on the site, as well as project goals regarding health. When these goals feel solid, the designer then moves to design ideas that meet those goals and address the site issues. The design ideas may stimulate additional project goals or reveal further issues on the site. Each of the design ideas is then extrapolated to predict individual and community health outcomes, as well as any unhealthy consequences of these actions. The designer then weighs the health and the unhealth and makes changes to the design. Lastly, the designer considers how each of these health outcomes might be evaluated, and what
resources are available to collect such data. Existing published literature and software modelling tools would be scanned to determine if previous studies have measured or correlated similar design concepts with health outcomes.
ideas,
the
Health
Impact
Assessment
framework used in the public health and planning professions, and Evidence Based Design practices. Complexity Theory understands that not all health outcomes could or should be measured, and that merely revealing a relationship is a strong discovery in itself (Mugerauer, 2010 and Mugerauer, 2012). The Health Impact Assessment tool is used to evaluate large scale policy, planning and design
Framework Strategy 3: Organic Flow
INDIVIDUAL HEALING
Strategy 3 seemed the most successful of the frameworks tested. The design team was able to follow the process and, by the end of the discussion, was using the word ‘health’ in conversation. Because
The framework is loosely based on Complexity Theory
Conclusion: A Health Framework Stimulates a Health Dialogue
it was tested on a theoretical student project, it is unclear just how helpful the framework is in creating smarter design, and more healthful outcomes, however the framework did stimulate dialogue centered around health and may have created an impact on these students learning to consider health, which is a first step. The following pages outline the testing of Strategy 3 on the design team.
Framework Strategy 3 Organic Flow Pros: • flexibility of framework embeds health dialogue within the creative design process • conversational and freeflowing • health outcomes open to being determined by published literature, modelling, professional opinion, or merely identifying positive correlations
EXISTING ISSUES
Cons: • unclear how helpful the framework is in creating more healthful outcomes • data collection potentially cumbersome (i.e. literature, modelling etc) to determine health outcomes
PROJECT GOALS
EVALUATION DATA DESIGN SCRIPTS
DATA RESOURCES POTENTIAL UNHEALTH
projects, and gives a value to precedent literature and professional opinion as accepted ways to predict health outcomes (Dannenberg et al, 2008). Evidence Based Design bases decisions about the built environment on credible research to predict outcomes (The Center for Health Design, 2008).
10
COMMUNITY HEALING
11
Testing the Framework
Participating Parties Framework Strategy 3, outlined in the previous pages, was tested on a student design team in the process of designing their capstone project. Due to time constraints and student schedules, the framework was not as in depth as it might be in the professional world, however a general testing of its potential is outlined in the following pages. The author of this thesis acted as the facilitator, or Health Champion, of the project and was involved from the very beginning stages of the project. It should be noted that the Health Champion has a background in landscape architecture, and, although has studied public and global health concepts in graduate school and practiced professionally in
professionals knowledgeable in both health and design, a few of which have practicing experience in both professions.
The Design Project Because of its dramatic health conditions, degraded maintenance regimes, entropic boundaries and migrating plumes, DIG Studio was interested in
Missing Stakeholders Because
this
framework
tests
a
theoretical
the conversation.
A lack of community or client
simplified the design process, however the design team did their best to consider cost barriers, cultural
three graduate landscape architects also without a health background. Together, the Health Champion and student design team make up DIG Studio.
design professionals
PARTICIPATORY PUBLIC MEETINGS + OUTREACH
EXISTING CONDITIONS ANALYSIS
AGENCY REPORTS + ANALYSIS
DESIGN MEETINGS
LAWS + POLICY
regulatory
client / operations
designing on a contaminated Superfund site. The site chosen is the McCormick and Baxter brownfield in the Port of Portland Superfund site along the WIllamette River in Portland OR. The design explores ways to harness natural processes to improve the health of the landscape and greater ecological system, as well as the health and wellbeing of the people in the community.
Timeline Because of
the testing of
prior unsuccessful
SITE LOCATION, FINANCING + OPERATIONS
frameworks, Strategy 3 was tested on DIG Studio after initial design brainstorming had already taken place, but before a schematic design had been formulated. DIG Studio chose to design on the McCormick and Baxter property adjacent to the University of Portland. This site is part of the Port of Portland Superfund site along the Willamette River just north of downtown Portland OR. [googlemaps]
They are advised by a collection of professors and
12
community
context and regulatory requirements.
ecological landscape design, does not have a formal health background. The design team is made up of
Participating Project Parties
Project Location
student project, stakeholders were missing from
13
3RD PARTY INTERPRETS // CONSOLIDATES // CATEGORIZES GOALS
Because the framework was tested on a student project, stakeholders such as the community and client were missing from the dialogue.
Health Definition
Goals The first step of the health framework identified
Next, DIG Studio formulated a project specific
existing issues and translated those issues into
definition of health that would act as an umbrella
goals of the project. Ideally, these goals would be
goal for the entire project. The definition allowed the
generated by all stakeholders, however as previously
design team to collectively discuss the relationship
mentioned, the client and community were lacking
between the goals and desired outcomes.
Ecological ecotones and edge conditions
The goals were generated collectively by
all students in DIG Studio, and were organized and translated by the Health Champion.
Categorizing
functioning ecosystem services
team came up with four categories for the goals: Ecological, Economic, Social, and Phenomenological or Experiential. Since many of the goals spanned multiple categories, a Venn diagram was formulated to express this relationship, shown to the far right.
weighing the goals and determining which design ideas make the cut.
learning lab
Overarching Definition of Health for the Project
multiple overlapping complementary systems
accessibility
compile the goals from all the stakeholders and
touch points
facilitate the sifting. Design ideas that hit the goals,
secure (crime)
HANGING DESIGN IDEAS
sift through. The Health Champion generally would
and especially those that hit multiple goals, will fall through and become the initial design.
Financial
constraints, constructability, cultural acceptance and other factors would act as “reality magnets,� drawing up design ideas that are not strong enough to bypass the reality check.
FUTURE DESIGN IDEAS
Some design ideas
might fall in the middle, to be saved for a later design reconnected fragmented landscapes
walkable destination / attraction neighborhood amenity / value
positive perception
phase or if any reality magnets decrease in strength.
social engagement safe (injury)
Social
14
diagram is visualized as a sieve that the design ideas
curiosity about site
sensory stimulation + excitement
Health: the combined effects of successive, evolving, and indeterminate landscape processes and management strategies on human well-being
To picture how this might
happen in relation to this framework, the goals
Phenomenological biodiversity
$$
The most difficult process of any design project is
economic draw / creative capital
the goals helped the design team to understand how they might translate into design aspects. The
CULTURE
Economic
from the discussion because it is a theoretical student project.
Weighing and Sifting
Categorized Health Goals of the Project
INITIAL DESIGN 15
CAPACITY
{ EXISTING ISSUES } of soil + water { contamination { PAH, arsenic, copper, lead existing cap function + failure { { fallow, unused site { { { no people + fear issues { no current function { { { overly controlled shoreline { fenced + inaccessible { { { access + wayfinding difficult { { perception of homeless {
Running Through the Framework The final step, which is really a series of steps, is An Outline of the Health Framework
running through the framework. DIG Studio revisited the goals and issues identified in the previous steps,
INDIVIDUAL HEALING
refining them throughout the weighing and sifting
{ DESIGN SCRIPTS } breaking of cap to release toxic { controlled { plumes + remediate with plant plumes dimples along shoreline that punch + treat { { contaminated soil below cap piling revealed with natural erosion over { sheet { time creating occupiable vs visual spaces bicycle access + connection to west { { side of river as glass bottom underwater { reusing bargesobservatories { remediation + monitoring cleanses, { nanotube { with interpretive light-up barometer particles inserted in river sediment, creates { nanojetty, { plant plume colonizes + breaks down floating islands become free floating river { cleanup tool, + create new remediating land { grading breaks up site monotany { { ADA accessibility { { { removal of fence, no tresspassing signs { { access to water recreation, recreational beach { continued rail line { { plant phasing to biodiversity (starts out with { monoculture poplar cleanup, insert species after){ indeterminate game fields { { to university, physically + with { connectionprogramming { elements (dog walking, running, { open to neighborhood { biking etc.) create attractive amenities { { { testing lab that educates, explores, creates jobs {
process. Design ideas were then brainstormed, and Testing the Health Framework
the Health Champion, based on literature review and professional experience, determined potential individual and community health outcomes for each.
EXISTING ISSUES
EVALUATION DATA DESIGN SCRIPTS
Any unhealth that appeared in the outcomes was
COMMUNITY HEALING
then communicated back to the design team, where they could weigh it and change the design if needed. The Health Champion then identified potential ways
DATA RESOURCES
PROJECT GOALS POTENTIAL UNHEALTH
that the health outcomes could be evaluated and how that data might be collected. Lastly, the framework was extrapolated to the site, to give spatial context to health outcomes.
16
A visual example of testing the health framework on the student design team. The diagram reveals relationships and connections between each aspect of the framework.
{ PROJECT GOALS } { ecotones + edge conditions { biodiversity { { { functioning ecosystem services { multiple overlapping { complementary { systems reconnected fragmented landscapes { { { economic draw / creative capital { learning lab { { accessibility { { { walkable destination / attraction { { neighborhood amenity / value { curiosity about site { { touch points { { { sensory stimulation + excitement { secure (crime) { { positive perception { { social engagement { { safe (injury) { {
17
{ INDIVIDUALHEALING } (sports, walking, running, { exercise { biking, crew launch platform) less chronic diseases { { less human { less contaminants{ vector pathways education { { individual jobs { { { income, business revenue { inspiration { { stimulation { { less injuries { { opportunities for play { { { less mental disease, depression { { COMMUNITYHEALING } less crime { { community access { { home values increase { { draw (research money, { university publicity, prospective students) { { social justice for neighborhood { { environmental stewardship { community education { { increased opportunities for {relationships with neighbors,families { community + university { partnerships { + programs healthier habitats { { { reduced carbon emissions { to west side { connecting community { of river {increase in community pride, visitors { { POTENTIALUNHEALTH } islands could get stuck in places, habitat issues { { undesirable { island conflicts with boats { { people running into nanotubes { { lighting + safety not addressed yet { of poplars would reduce habitat at first { monoculture { areas undesirable for walking to elevate boardwalk) { wet(need { - sediments may at first destroy aquatic habitat { erosion { { rail conflicts with safety { { erosion- safety with mudslides { shore edge safety { { {poplars may agitate asthma/allergies { { limited emergency access { of bacteria / micorrhizal { spreading contamination of neighborhood {
{ EVALUATION DATA } action, location { on-site +people, { quality counts fauna, soil, water { on-siteairflora, { + quality counts grade, attendance { { + education reports crime + injury reports { { { property + business revenue reports { { demographic + income GIS data { { insurance company data { { neighbor observations + opinions { { user observations + opinions { current + historic aerial + { on-ground { photos + video current news, magazine, blog { articles + social networking sites { regulatory reports { { { DATA RESOURCES } interviews { { in-field questionaires { { mailed questionaires { { site observations { { video surveillance { { { online blog + social networking sites { on-site monitoring { automaticequipment { measurements + { expert on-site { data collection insurance companies { { census + city data { { { university + nearby schools { { police and emergency services { local + county auditor { { published literature { { + archival records { historic { online + in local library { local, state, federal agencies {
Design Interventions and Potential Physical and Health Outcomes Over Time
Application of Health to the Design
~
health framework could affect
with
POINTS
potential EXISTING R A I L BRIDGE
physical outcomes predicted over time.
Each potential physical
outcome in
terms
then of
was
evaluated
individual
and
community health. The diagram
+
q STRESS
+
~
WILLAMETTE WATER
~
~
~
BARGE ON END
DERELICT BARGES ARE USED AS MARKERS FOR CHANGE, AND SUPPORTS FOR NEW PED/BIKE INFRASTURCE
+
PATHS
AND EDGE CONDITIONS
The
+
+
p PEOPLE ON SITE
as potentially negative health outcomes were identified, each line
indicating
or relationship. outcomes
are
a
correlation
Some health yet
unknown,
visualized by the blank circles.
~
p INJURIES
+
p WALKABILITY
+
q CHRONIC ILLNESSES
AMENITY
+
+
p MENTAL WELLBEING
q CRIME
+
p PROPERTY VALUES
+
p COMMUNITY PRIDE
+
p TOURISM
18
p GENTRIFICATION
p NEIGHBORHOOD
that double as identified goals Positive as well
~
+
p SOCIAL COHESION
+
p ECONOMIC DRAW
XXX
XXX
XXX XXX
XXX
XXX
RIVER SCORE CONDITION: CONTAMINATED RIVER SEDIMENT
XXX
~
q TOUCH
POINTS
TO ADVERSITY
+
~
+
ATTENTION
~
TREE Y
p SOCIAL JUSTICE
+
+
X3YR
Y1YR
PLUME X
PLUME Y
SURVEYED EDGE
SURVEYED EDGE
q SOCIAL ENGAGEMENT
Y3YR
PLUME X
~
+
p GENTRIFICATION
p NEIGHBORHOOD
+
AMENITY
+
1
A
~
+
+
p WALKABILITY
p INJURIES
X
ILLNESSES
+
Y
p MENTAL WELLBEING
q CHRONIC
+
FALLOW SCORE A INSERTION: PLUME; SUBSET INTRUCTIONS: RIGID PATH REPEAT STEPS 1-3 EVERY 12 MONTHS
+
q CRIME
REPEAT.REPEAT.REPEAT
PLUME Y SURVEYED EDGE
~
X5YR
+
+
PLUME Y
p TOURISM
p ECONOMIC DRAW
SURVEYED EDGE
+
PLUME X SURVEYED EDGE
2
FALLOW SCORE B INSERTION: PLUME; FLEX PATH
+
3
FALLOW SCORE B INSERTION: PLUME; FLEX PATH
+ +
X
Y
Z
X
WETLAND
+
+
SCORE +FALLOWRIPARIAN FLOOD 2-1
Z
PLAIN
REPEAT.REPEAT.REPEAT
+
+ X3YR
Y1YR
Y3YR
COLONIZATION
+
PLUME X
PLUME Y
SURVEYED EDGE
SURVEYED EDGE 2
PLUME X
+
X5YR
RIVER SCORE A FALLOW SCORE B INSERTION: PLUME; PLUME X SURVEYED EDGE FLEX PLAN 3 FALLOW SCORE B INSERTION: PLUME; FLEX PATH
+
~
+
+
SUBSET INTRUCTIONS: REPEAT STEPS 1-3 EVERY 12 MONTHS REPEAT X 5YR. PLUME X OVERTAKES PLUME Y
1
RIVER SCORE A
~
X5YR
PLUME X SURVEYED EDGE
B3
+
+
Y
Z
FALLOW SCORE INSERTION: PLUME; FLEX PATH
~
+ +
19
+
~ +
+ X
SURVEYED EDGE 2
FALLOW SCORE B INSERTION: PLUME; FLEX PATH
~
+
+
~
PLUME Y
SURVEYED EDGE
~
+ +
Y
2
FALLOW SCORE A INSERTION: PLUME; SUBSET INTRUCTIONS: RIGID PATH REPEAT STEPS 1-3 EVERY 12 MONTHS
Y
+
p MENTAL WELLBEING
p SENSORY STIMULATION
Y3YR
SURVEYED EDGE
q STRESS
+
PRIDE
PLUME X
+
+
p CURIOSITY ABOUT SITE
POINTS
SUBSET INTRUCTIONS: REPEAT STEPS 1-3 EVERY 12 MONTHS REPEAT X 5YR. PLUME X OVERTAKES PLUME Y
p COMMUNITY
+ X
p ENVIRON. STEWARDSHIP
p TOUCH
p JOBS
p PROPERTY VALUES
AMENITY
+
+
Y
Z
+
pNEIGHBORHOOD
+
+
2-1
FALLOW SCORE RIPARIAN FLOOD PLAIN
+
X3YR
PLUME X
X
p PROPERTY VALUES
Z
+
+
p HABITAT
2-1
FALLOW SCORE RIPARIAN FLOOD PLAIN
LAB
+
SUBSET INTRUCTIONS: B. PLANT PLUME NODES 1. SURVEY EVERY 12 MONTHS FOR EDGE DELINEATION (PLANT HEIGHT & CONCENTRATION ) Z 2. INSTALL ELEVATED MODULAR GRATE PATH AT EDGE 3. @1 YEAR: REMOVE & REINSTALL PATH AT NEW SURVEYED EDGE SUBSET INTRUCTIONS: REPEAT STEPS 1-3 EVERY 12 MONTHS REPEAT STEPS 1-3 EVERY 12 MONTHS REPEAT X 5YR. PLUME X OVERTAKES PLUME Y
~
p BIODIVERSITY
SERVICES
FALLOW SCORE B INSERTION: PLUME; FLEX PATH
p LEARNING
SURVEYED EDGE
~
+
p FUNCTIONING
2
SCORE A FALLOW SCOREFALLOW INSERTION: PLUME; INSERTION: PLUME; RIGID PATH RIGID PATH 2
PLUME Y
SURVEYED EDGEECOSYSTEM
SURVEYED EDGE
FALLOW SCORE B INSERTION: PLUME; FLEX PLAN
GRASS Z
+
p SOCIAL COHESION
Y1YR
X1YR
+
~
SUBSET INTRUCTIONS: REPEAT STEPS 1-3 EVERY 12 MONTHS REPEAT.REPEAT.REPEAT
+
~
~
+
FALLOW SCORE A INSERTION: PLUME; RIGID PLAN
p PEOPLE ON SITE
FALLOW SCORE B INSERTION: PLUME; FLEX PLAN
p REGULATORY
RIVER SCORE A INSERTION: NANOBUCKS> JETTY
+
PATHS
p ACCESSIBLE
Y
X1YR
Y
Z
X1YR
2
+
p HUMAN VECTOR PATHWAYS
BARGE ON END
Z
p CHRONIC ILLNESSES
X
Y
FRAGMENTED LANDSCAPES
SUBSET INTRUCTIONS: B. PLANT PLUME NODES 1. SURVEY EVERY 12 MONTHS FOR EDGE DELINEATION (PLANT HEIGHT & CONCENTRATION ) 2. INSTALL ELEVATED MODULAR GRATE PATH AT EDGE 3. @1 YEAR: REMOVE & REINSTALL PATH AT NEW SURVEYED EDGE REPEAT STEPS 1-3 EVERY 12 MONTHS
~
WILLAMETTE RIVER EXISTING RIVER SEDIMENT
2-1
FALLOW SCORE RIPARIAN FLOOD PLAIN
Z
p RECONNECT
~ X
~
p MENTAL WELLBEING
+
2
FALLOW SCORE A INSERTION: PLUME; RIGID PATH
SUBSET INTRUCTIONS: B. PLANT PLUME NODES 1. SURVEY EVERY 12 MONTHS FOR EDGE DELINEATION (PLANT HEIGHT & CONCENTRATION ) 2. INSTALL ELEVATED MODULAR GRATE PATH AT EDGE 3. @1 YEAR: REMOVE & REINSTALL PATH AT NEW SURVEYED EDGE REPEAT STEPS 1-3 EVERY 12 MONTHS
p RESILIENCY
p EDUCATION
1
q STRESS
+
+
GRASS Q p HUMAN VECTOR PATHWAYS
ADDITION
DERELICT BARGES ARE USED AS MARKERS FOR CHANGE, AND SUPPORTS FOR NEW PED/BIKE INFRASTURCE
~
~
q ECOTONES
p SOCIAL JUSTICE
FALLOW SCORE A INSERTION: PLUME; RIGID PATH
+
TREE X
~
FALLOW PATCH MCORMICK & BAXTER, ARKEMA
q BIODIVERSITY
CAP
+
p SENSORY STIMULATION
RIVERBED
~
~
qFUNCTIONING
~
+
POINTS
~
~
+
~
X
EXISTING R A I L BRIDGE
~
FALLOW SCORE A INSERTION: PLUME; RIGID PATH
1
~
p TOUCH
q ENVIR. STEWARDSHIP
+
p ACCESSIBLE
GRASS Z
WILLAMETTE WATER
ECOSYSTEM SERVICES
~
+
p INJURIES
~
q FUNCTIONING
DECREASE
p MENTAL WELLBEING
FALLOW SCORE A INSERTION: PLUME; RIGID PLAN
BARGE ON END
RIVERBED
INCREASE
q
GRASS Z
+
FRAGMENTED LANDSCAPES
POTENTIAL FOR HEALTHFUL OUTCOME
p
FALLOW SCORE A INSERTION: PLUME; RIGID PLAN
p RECONNECT
blue circles are health outcomes of the project.
TREE X
TREE Y
TO ADVERSITY
POTENTIAL FOR UN-HEALTHFUL OUTCOME
TREE Y
~
BARGE
p RESILIENCY
p EDUCATION
TREE X
RIGID PLAN
CAP BROKEN
~
to the near right displays one such design intervention.
BARGE BURNERS>
GRASS Q
+
ADDITION
BARGE X, Y & Z LEFT TO RUST> IRON PLUME
BARGE INSERTED INTO BLUFF> BLUFF PIER
~
+
+
p HUMAN VECTOR PATHWAYS
p TOUCH
key design interventions were out,
+
ABANDONED
~
+
BARGE ON END
BIRCH PLUME PROVIDES PERCHING SITES, > SECONDARY PLUME IS VIA SEED DISPERSAL
BREAK CAP
p SENSORY STIMULATION
p INJURIES
diagrams were created. Several
~+
1
FALLOW SCORE A INSERTION: PLUME; RIGID PATH
FALLOW SCORE A
PLUME; HEALTHINSERTION: SYMBOLOGY
GRASS Q
To better understand how the
mapped
p MENTAL WELLBEING
Potential Health Outcomes
design and outcomes, a series of
GRASS Z
SCENARIO SYMBOLOGY
GAME 4 // McCORMICK & BAXTER
Understanding the Framework
+
An Isolated Design Intervention and Its
TREE Y
~
{ design }
POTENTIAL HEALTH OUTCOMES MENTALWELLBEING
-$ +$ -$
processes. = PUBLIC ACCESSIBLE
implications of the design. While the designers were
outcomes.
aware to some degree of potential physical outcomes and their effects on human health, this process was
The diagram to the immediate right isolates one
helpful in communicating the extent of the “ripple
script idea. Sheet piling will be added to a shoreline
effect” and those indirect health consequences often
area, revealing a public pathway with natural erosion
left out of the design conversation.
Outcomes within the health brackets 20
Pb Pb
Pb
As
+
=
= PUBLIC ACCESSIBLE
20FT
REFLECTION STEWARDSHIP
REMISLANDCONFLICTS
+$
+$
+
-$ +$ -$
-$
+$
+$
+$
NEIGHBORHOODAMENITY
+$
DECONTAMINATIONAQUATIC HEALTH
-$ +$ -$
-$
+$
+
GROUNDWATER
PHYSICALHEALTHCHRONICILLNESSES
SEDIMENTATIONAQUATIC HEALTH
21
+ + + + +++ + + + CONTAMINATED
PUBLIC EDUCATION
PHYSICALHEALTHCHRONICILLNESSES
REMISLAND
= NANOTUBE
& H
Cl
PAH
, INDETERMINANTGAMEFIELDS
+ WASTEWATER
EFFLUENT
= WILLOW
BIRCH
H C
Cd
C
Cl
BIODEGRADATION OGRANICCHEMS
BIND+SEQUESTER
=
+
CLEANSED WATER
CLEANWATER FLOATINGHABITAT
=
-$
BIODEGRADATION
=
Cd
HEAVYMETAL ORGANICCHEMICAL
BIRCH
ACCUMULATION
FT
15
60°
+
WILLOW
Cl
SEQUESTRATION
Pb
Cd
PARTNERSHIPS
H C C
BIRCH & ASPEN PLANTING
+
COMMUNITYUNIVERSITY
H
POPLARS
SEQUESTRATION
=
FERN
NANOTUBE
& Cl
ENDOPHYTE++
EFFLUENT TREATMENT BIOFUEL PRODUCTION STORMWATER DETENTION
helpful in understanding the complexity of health
=
+
Cl
FILTER+DEGRADE
The visual evaluation of each design intervention was
+
MENTALWELLBEING
EDUCATION PROCESSES
Pb
PROPERTYVALUES
PUBLIC ACCESSIBLE
+$
FERN
CLEANSED WATER
PATHWAY REVEALED
=
ECOSYSTEMSERVICES
based research to predict the likelihood of health
EROSIONACCUMULATION NEARSHOREHABITAT
activity.
Pb
REFORESTATION HABITAT
C
Pb
Pb
HABITAT
H C
EDUCATION PROCESSES
+$
+
HEALTHY SOIL
H
Cl
CHEMICAL
= PUBLIC ACCESSIBLE
As
FILTER+DEGRADE
EROSIONTURBIDITY AQUATICUNHEALTH
=
PATHWAY REVEALED
EROSIONACCUMULATION NEARSHOREHABITAT
30FT
15FT
with additional design scripts added to move it back
economical, nutritional and wellbeing aspects of the
POPLARS
20FT
+
health definition and goals, would be reexamined,
Unhealth Outcomes
EROSIONTURBIDITY AQUATICUNHEALTH
+$
ENDOPHYTE++
SHORE PINE PLANTING
and Potential Health and
opportunities for fishing and the recreational,
fall outside the brackets of the predetermined
Cl
RESEARCH JOBS
activity, reducing the probability of diabetes and
balancing out the food chain and providing increased
as to the potential health outcome, and those that
=
+
C
+
Design Interventions
habitat increases aquatic health, contributing to
that each design script insertion would be evaluated
H C
CHEMICAL
POPLAR PLANTING
+$ H
Cl
MONOCULTURE
opportunity for recreation and increased physical other chronic illnesses. The creation of nearshore
often used in contemporary practice. The idea is
EDUCATION INSPIRATION
RESEARCH JOBS
REUSED/REBUILT BARGE FOLLIES
0”
instead of a concrete masterplan as the goal, as is
MENTALWELLBEING
REUSED/REBUILT BARGE FOLLIES
+
20FT
would initiate processes, using health as a goal
over time.
natural
health problems. An accessible pathway provides the
These scripts
would facilitate this evaluation, utilizing evidence-
of
affect one’s ability to deal with mental and physical
not developed. Instead, a fluid, initial masterplan
into the accepted brackets. The Health Champion
education
to improve resilience to life challenges, and can
eventually health outcomes, a static masterplan was was drawn using design “scripts.”
ecological
Education and stimulation in outdoor areas is known
An Isolated Design Intervention and Its Potential Health Outcomes + Evaluation
interventions can stimulate natural processes, and
making the site publicly accessible, and promoting
MENTALWELLBEING
Because DIG Studio was interested in how design
+$
PHYSICALHEALTHCHRONICILLNESSES
RESEARCH JOBS
indeterminate design + health outcomes
include creating a healthy nearshore habitat area,
RMICK & BAXTER HEALTH
Applied Results
-$
INSTALL SCRIPTS
Conclusion
References
A New Approach: Health Within the Design Conversation In sum, a dialogue about health taking place within
By testing the health framework on a university
the design process could create more salubrious
design project, the role of the Health Champion, and
design and positive health outcomes on people,
the feasibility of the framework was explored. While
landscapes and ecologies.
the DIG Studio project was a theoretical student
The findings in the
following pages may identify a need for:
project, lacking many constraints and input found in the professional world, the framework did appear
• •
•
•
Health goals to be defined by all stakeholders
to embed health into the design conversation, which
A 3rd party Health Champion to help navigate
is reflected in the design. Furthermore, the Health
and communicate between health and design
Champion was able to communicate the “ripple
professionals, as well as stakeholders and the
effect” and those indirect health consequences
public
(both negative and positive) often left out of the
A framework to guide designers and help them
design conversation. Further exploration is needed
understand the health consequences of their
to determine the actual success of the framework,
design actions
but the health dialogue within the design process
Further dialogue centered around heatlh in
was a positive first step.
Application of Health to the Design (ATSDR). U.S. Department of Health and Human Services, Agency for Toxic Substances and Disease Registry. (2010). Leading changes for healthy communities and successful land reuse. Dannenberg, A. L., Bhatia, R., Cole, B. L., Heaton, S. K., Feldman, J. D., & Rutt, C. D. (January 01, 2008). Use of health impact assessment in the U.S.: 27 case studies, 1999-2007. American Journal of Preventive Medicine, 34, 3, 241-56. Mugerauer, R. (December 01, 2010). Toward a Theory of Integrated Urban Ecology: Complementing Pickett et al.Ecology & Society, 15, 4.) Mugerauer, R. (2012, May 23). [Lecture]. Complexity Theory, Qualitative Research Methods, University of Washington. The Center for Health Design. (2008). Definition of EvidenceBased Design for Healthcare. Retrieved May 13, 2012, from http://www.healthdesign.org/aboutus/mission/EBD_ definition.php
design
22
23
RESEARCH + EVALUATION IN THE DESIGN PROCESS
HEALTH EVALUATION
01
RESEARCH + EVALUATION IN THE DESIGN PROCESS
HEALTH EVALUATION
Introduction
Current Trends in Research + Design
A Need for Health Research and Evaluation
Design and research are often viewed as two separate disciplines that rarely cross paths. Very
While
few projects have an appropriate budget for
architects, are trained to have a basic understanding
research and evaluation (if any at all) and the little
of many different disciplines and topics, designers
that is conducted often occurs before a designer
rarely are required to understand health. Other than
enters the picture or after the designer is finished,
safety issues, health concepts are not incorporated
missing valuable cross-pollination of information.
in the training or licensing of landscape architects.
designers,
and
particularly
landscape
Organizations such as the Environmental Design and Research Association (EDRA) are working to
This used to be the case in understanding
weave the perceived academic and professional
environmental sustainability and ecological systems,
disciplines together and incorporate research more
however with current market trends favoring “green”
within the design process, and many high profile
and sustainable practices, designers were forced to
design projects are beginning to prioritize research,
learn these concepts in order to please their clients
however mainstream practice does not reflect
and win proposals. To cater to this growing need
this trend.
Misunderstandings and stereotypes
to understand and predict environmental outcomes,
between professionals, differences in training and
a series of tools and metrics were developed for
communication, and a lack of prioritization from
designers (i.e. LEED, SITES etc.). While not every
clients may be to blame. However, recent inquiries
design gets LEED certified, the knowledge of
into how the built environment affects health may
sustainability is transferred to coworkers, other
call for a renewed interest in the integration of
projects, and the next generation of designers.
research and design.
Eventually, concepts of sustainability may become
02
such common knowledge and practice that the LEED framework may become obsolete.
While
funding might not be there just yet, the conversation of monitoring and evaluating projects to measure environmental
outcomes
is
becoming
more
commonplace. This conversation may trickle down to influence market demand and client desires, to prioritize research in every stage of the design. Furthermore, desires for adaptive management practices may create a need for ongoing evaluation of environmental outcomes. The growing interest in health and design may follow a similar pathway. Tools could be developed to help designers understand and predict health outcomes. Projects may incorporate monitoring and research to determine how the design affected health in a given community. Long-term monitoring may be desired to fulfill adaptive management trends. Eventually, tools and frameworks to help designers understand health in their design may disappear and a health focus in design could become the new ‘norm.’
03
Research in Every Project Stage
Feedback Loop
To maximize understanding of health outcomes,
The value of full project research and evaluation
research should occur in every stage of the project.
lies in the feedback loop. Field research is affected
Research can be a valuable tool in both predicting
by many different external and internal factors and
and reflecting on health outcomes. Before design,
Research in Each Project Stage to Maximize
tests are not able to be isolated in the way they are
baseline data can be collected to determine
Understanding of Health Outcomes
in the lab. Because of this, the literature database
During design, evidence-
based design methods such as a literature or case study review can help predict health outcomes to inform design strategies.
E BAS
LINE D
ATA COLLEC TION
EXISTING CONDITIONS
ERA LIT
HEALTH OUTCOME
DESIGN
After construction,
a follow-up evaluation can help determine actual health outcomes. Since health requires time and periodic reflection, ongoing monitoring is best to
pre-design process
design process
needs to be quite large to account for errors and
OING MONITORING ONG
EBD PRIN TURE + CIPA LS
misinterpreted correlations.
BUILT PROJECT
evaluation process
actual
preexisting conditions.
predicted
Complete Health Research + Feedback
Health-Design Feedback Loop
By monitoring the
project and sharing results, the literature and case study database can grow and designers can have
LITERATURE EVIDENCE
LITERATURE EVIDENCE
MONITORING + EVALUATION
more information to reflect upon. Sharing research
HEALTH + DESIGN PROJECT
can, in turn, help inform other projects in an interconnected feedback loop.
LITERATURE EVIDENCE
In order for the feedback loop to be fully effective, While research in every project stage is ideal, it is
honest transparency of outcomes must be shared,
incredibly difficult to accomplish.
including both successes and failures.
This
be expensive and funding is often not available for
unfortunately is often not the case, since job
evaluation or long-term monitoring. After the project
reputations,
is built, clients may feel satisfied and not interested
and professional pride often get in the way of full
in researching for the “greater good.” Lastly, project
disclosure.
funder
expectations,
stakeholders
players will likely change over time, and with it the desire to follow through with evaluation. 04
HEALTH + DESIGN PROJECT
HEALTH + DESIGN PROJECT
determine long-term health outcomes.
Research can
Health-Design Feedback Loop and a Growing Database
05
MONITORING + EVALUATION
MONITORING + EVALUATION
HEALTH + DESIGN PROJECT
LITERATURE EVIDENCE
MONITORING + EVALUATION
Evaluation Precedents
There are many existing tactics and tools for predicting and determining outcomes in the built environment. The following section outlines the existing methods for pre-design data collection, tools that help predict outcomes, and methods/tools that evaluate outcomes after construction. While most of these “metrics” quantify outcomes, the last section examines precedents that measure quality and experience. Both quantification of scientific outcomes and examining quality of experiential outcomes are important in health-design practices.
Methods for Existing Data Collection Gathering existing data can utilize traditional research methods in the natural, social, economic and health sciences. reports
identify
Surveys and geotechnical
existing
landform
conditions.
Public meetings, interviews, questionnaires and site observations can establish baseline community perception, opinion and use of the site. Health data requires a much more extensive process, but utilizes similar qualitative tactics as well as quantitative health records and public health statistics.
06
ecological quality outcomes for designed wetlands,
Tools to Predict Outcomes During Design The recent burst of
called a Vegetated Index of Biological Integrity
“metrics” in the design
profession responds to a growing interest in predicting quantitative outcomes of design.
Most
of these tools revolve around the “green” movement to help identify environmentally sustainable layers in a design. Design tools such as LEED (Leadership in Energy and Environmental Design), LEED-ND (LEED Neighborhood Development), SITES (Sustainable Sites
Initiative),
and
SEED
(Social
Economic
Environmental Design) run a design through a metric with the aim to achieve a certain amount of points, reflective of environmental outcomes of the design.
While these metrics are voluntary
with certification and positive marketing as the goal, several have become local code or required by regulatory agencies.
Precedent Tools for Predicting Outcomes During Design
(VIBI). The National Environmental Policy Act (NEPA)
The Seattle Green Factor
(SGF) is a mandatory metric aimed at decreasing permeable surfaces, and predicting environmental outcomes in Seattle. The Environmental Protection Agency (EPA) requires a certain “score” predicting
requires an Environmental Impact Statement (EIS)
Launch
Subject
suggesting alternative solutions.
EPA VIBI
2007
Biodiversity
The Health Impact Assessment (HIA) is similar
HIA
2002
Human Health
LEED
2000
Environmental + Energy Sustainability
LEED-ND
2009
Environmental + Energy Sustainability
NEPA EIS
1970
Environmental Risk Assessment
SEED
2009
Social, Environmental + Economic Sustainability
Decision Makers, Agencies BE Designers, Community Leaders
SGF
2009
Quantity + Quality of Landscaping
SITES
2010pilot
Sustainable Land Design, Construction + Maintenance
for federal public projects describing the anticipated environmental effects of a proposed action and
to the EIS only it anticipates issues regarding human health for projects or policies. The HIA is conducted by planners or public health officials and shares recommendations to decision-makers how a project or policy could be improved to maximize health outcomes.
While the HIA is voluntary in
most situations, a few local governments around the nation are requiring HIAs for large scale public projects. Other evidence-based design practices can be employed to predict outcomes and validate design choices such as modelling, simulations, iterative testing + evaluation, learning labs and mock-ups testing usability or functionality.
07
Audience
Reach
Structure
Media
National
Regulation for Wetlands
Paper Submittal, Human Reviewer
International
Volunteer Assessment
Online Resources
BE Designers, Clients
International
Volunteer Certification
BE Designers Clients
International
Volunteer Certification
National
Regulation / Permit
Paper Submittal, Human Reviewer
National
Volunteer Certification
Online Documentation, Human Reviewer
BE Designers, Developers
City of Seattle
Regulation for New Development
Excel Worksheet, Human Reviewer
Land Designers, Clients, Maintenance
National
Volunteer Certification
Pilot Program Stage
Biologists, Wetland Designers, Clients Planners, Policy Makers, Public Health Officials
Online Documentation, Human Reviewer Online Documentation, Human Reviewer
Tools for Evaluation of Outcomes
Precedents for Qualitative Evaluation
Gathering data after a project is built can help
While there are many precedent tools and methods
determine the success of the outcomes.
that help gather quantitative data to predict and
Precedents Evaluating Human Experience and Quality Similar
Precedent Tools for Evaluating Outcomes Post Construction
tactics can be used as in existing data collection such as public meetings, interviews, questionnaires
Launch
Subject
Audience
Reach
Structure
Media
2003
Sustainable Land Management Practices
Land Managers, Construction Managers, Maintenance
Pacific NW Region
Volunteer Certification
In Person Assessment
Public Education
In Person Surveys
and site observations. There are several precedent tools and metrics that assist in evaluating specific
Salmon-Safe
outcomes. These tools can help quantify impacts and are helpful for designers and decision-makers to reflect on outcomes and make changes to achieve a better “score.” Salmon-Safe Certification evaluates sites and campuses on their efforts to treat stormwater and protect native salmon in the Pacific Northwest. The STAR Community Index evaluates local government’s initiatives to create sustainable communities
and
STARS,
the
Sustainability
Tracking, Assessment and Rating System helps
2011
STAR
2012pilot
Sustainable Livable Communities
Local Governments, Communities, Planners
National
2008
Environmental, Economic + Social Sustainability
Colleges + Universities
2007
Physical Health + Wellbeing
General Public, Planners
Walkscore
Mental Health + Wellbeing
science
based
outcomes,
Public Officials, City of Seattle General Public
experiential or emotional outcomes are much more perceptions are important to understand to maximize human experience and satisfaction. These factors, in turn affect human happiness and wellbeing, which is linked to positive health outcomes.
Interviews,
questionnaires, and narratives are typical methods Volunteer Rating
Pilot Program Stage
International
Volunteer Certification
Online Documentation, Human Reviewer
National
Public Education
Online Evaluation
for collecting experiential data, however there are several precedents outside the typical design professions that could also be studied.
Olympic
figure skating and rhythmic gymnastics as well as competitive dancing utilize metrics to score on presentation and artistry.
The Academy Awards,
colleges and universities evaluate their sustainable
Tonys and Grammys evaluate and rank movies,
initiatives. Walkscore is an evaluation of walkability
musicals and music based on personal preferences.
in communities around the nation. Lastly, the Seattle
Lastly, many Eastern cultures evaluate the quality
Happiness Report Card uses surveys to determine
and energy of a space based on Feng Shui Scores.
Academy Awards
movies
24 categories, score based on personal preference
Reach
Structure
Media
International
5,500 members vote for best picture, each professional votes for their expertise, if get 20% of votes you are nominated, most votes win an Oscar
In Person Event
Feng Shui Scores
quality of furniture space, flow placement per size of life energy + type of room
National Youth Ballet Competition
performance art
classical technical ability, performance quality + distinction
National
arts + sports
technical merit + presentation/ artistry
International
arts + sports
execution + composite score (artistic + difficulty)
International
Olympic Figure Skating Olympic Rhythmic Gymnastics
the happiness “score” in the city.
08
Scoring Categories
qualitative
challenging to measure. In design, emotions and
Seattle Happiness Report Card
STARS
evaluate
Subject
09
Personal
lose points for items on the floor and incorrect orientation of the house, rooms, and furniture, gain points for lucky items judged in a technique class + classical repertoire performance that every dancer learns so can easily compare technique + performance against other competitors 9 international judges, computer picks 7 scores randomly, tricks scored for execution and degree of difficulty by computer execution starts at 10.0 and deducted for technical faults, artistry is quality of music + choreography, difficulty is quality of skills performed
Online Calculator
In Person Event
In Person Event
In Person Event
Visual Example of the Health Research Framework for DIG Studio’s Design
Testing the Health Research Process
existing conditions research
Framework for Incorporating Research in Every Project Stage
Method for Complete Research and Evaluation
in the full life of the project and understand the The
framework begins by collecting existing data to
EXISTING ISSUES
health outcomes by using evidence-based design practices.
without a client or community, research on existing conditions was not as in-depth as it could be. EVALUATION DATA
DESIGN SCRIPTS
establish baseline conditions. While in the design process, the framework identifies a need to predict
Because DIG Studio’s project is theoretical and
INDIVIDUAL HEALING
health implications of the design. This framework was tested on DIG Studio’s design process.
Testing: Existing Conditions Data Collection
An Outline of the Health Framework +
A framework was developed to incorporate research
COMMUNITY HEALING
outcomes. This framework is visually depicted in
said, DIG Studio was able to collect data on the concerns of contaminants present on the site from
incorporating evaluation and long-term monitoring to determine the level of success and the actual health
for existing baseline health conditions, obtaining
existing environmental conditions and the health POTENTIAL UNHEALTH
Finally, the framework recommends
Ideally, the community wouldl be closely studied both medical statistics and personal opinions. That
DATA RESOURCES
PROJECT GOALS
EPA and Department of Ecology reports due to the existing conditions research
predicting design-health outcomes using EBD principles
evaluation of outcomes
Superfund status and cleanup efforts. Additional physical data was also collected from topographic
a, outline to the right, and a more complex visual
and aerial mapping, and census demographics
example of DIG Studio’s design in the framework to
and GIS data painted a picture of the existing
the far right.
social and economic conditions of the community. Furthermore, site visits were conducted to obtain
{ EXISTING ISSUES } of soil + water { contamination { PAH, arsenic, copper, lead { existing cap function + failure { fallow, unused site { { { no people + fear issues { no current function { { { overly controlled shoreline { fenced + inaccessible { { { access + wayfinding difficult { { perception of homeless { { PROJECT GOALS } { ecotones + edge conditions { biodiversity { { { functioning ecosystem services { multiple overlapping { complementary { systems {reconnected fragmented landscapes { { economic draw / creative capital { learning lab { { accessibility { { walkable destination / attraction { { { neighborhood amenity / value { curiosity about site { { touch points { { { sensory stimulation + excitement { secure (crime) { { positive perception { { social engagement { { safe (injury) { {
additional information such as personal experience, neighborhood
perceptions,
human
scale
site
interactions, and sight views.
10
predicting design-health outcomes
11
{ DESIGN SCRIPTS } breaking of cap to release toxic { controlled { plumes + remediate with plant plumes along shoreline that punch + treat { dimplescontaminated { soil below cap piling revealed with natural erosion over { sheet { time creating occupiable vs visual spaces bicycle access + connection to west { { side of river as glass bottom underwater { reusing bargesobservatories { remediation + monitoring cleanses, { nanotube { with interpretive light-up barometer particles inserted in river sediment, creates { nanojetty, { plant plume colonizes + breaks down floating islands become free floating river { cleanup tool, + create new remediating land { grading breaks up site monotony { { ADA accessibility { { removal of fence, no trespassing signs { { { access to water recreation, recreational beach { continued rail line { { plant phasing to biodiversity (starts out with { monoculture poplar cleanup, insert species after){ indeterminate game fields { { to university, physically + with { connectionprogramming { elements (dog walking, running, { open to neighborhood { biking etc.) create attractive amenities { { { testing lab that educates, explores, creates jobs {
{ INDIVIDUALHEALING } (sports, walking, running, { exercise { biking, crew launch platform) less chronic diseases { { less human { less contaminants{ vector pathways education { { individual jobs { { { income, business revenue { inspiration { { stimulation { { less injuries { { opportunities for play { { { less mental disease, depression { { COMMUNITYHEALING } less crime { { community access { { home values increase { { draw (research money, { university publicity, prospective students) { { social justice for neighborhood { { environmental stewardship { community education { { increased opportunities for {relationships with neighbors,families { community + university { partnerships { + programs healthier habitats { { { reduced carbon emissions { to west side { connecting community { of river {increase in community pride, visitors { { POTENTIALUNHEALTH } islands could get stuck in places, habitat issues { { undesirable { island conflicts with boats { { people running into nanotubes { { lighting + safety not addressed yet { of poplars would reduce habitat at first { monoculture { areas undesirable for walking to elevate boardwalk) { wet(need { erosion - sediments may at first destroy aquatic habitat { { { rail conflicts with safety { { erosion- safety with mudslides { shore edge safety { { {poplars may agitate asthma/allergies { { limited emergency access { of bacteria / mycorrhizal { spreading contamination of neighborhood {
potential evaluation of outcomes
{ EVALUATION DATA } action, location { on-site +people, { quality counts fauna, soil, water { on-siteairflora, { + quality counts grade, attendance { { + education reports crime + injury reports { { { property + business revenue reports { { demographic + income GIS data { { insurance company data { { neighbor observations + opinions { { user observations + opinions { current + historic aerial + { on-ground { photos + video current news, magazine, blog { articles + social networking sites { regulatory reports { { { DATA RESOURCES } interviews { { in-field questionaires { { mailed questionnaires { { site observations { { video surveillance { { { online blog + social networking sites { on-site monitoring { automaticequipment { measurements + { expert on-site { data collection insurance companies { { census + city data { { { university + nearby schools { { police and emergency services { local + county auditor { { published literature { { + archival records { historic { online + in local library { local, state, federal agencies {
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16
predicted health + wellbeing outcomes
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design element example
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p
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Health is an incredibly challenging outcome to
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Challenges with Evaluating Health
evaluate in the field. Because so many aspects of
hi
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Visual Example of Evaluating Outcomes of One Goal of One Design Element
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ns
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tio va er s ob
rep or t s
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Because DIG Studio’s design is a theoretical project that won’t be constructed, a research
NEWSPAPERS, POLICE SERVICES, INTERVIEWS QUESTIONNAIRES, CENSUS + CITY DATA INTERVIEWS, INTERVIEWS, QUESTIONNAIRES, QUESTIONNAIRES, SOCIAL NEWSPAPERS, NETWORKING ONLINE BLOG
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Testing: Health Outcomes After Construction
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for health changes.
Many health issues, such
as cancer, take years to develop, and therefore
are not always truthful or willing to talk. Medical records and physicians are held to confidential
physicians + surgeons physicians assistants
planners
nurses
surveyors construction managers + contractors
place because of a lack of funding, patience, or Health is a sensitive topic, and people
HEALTH PROFESSIONALS
natural, social, economic, design researchers
require long-term studies of that may not take interest.
RESEARCH PROFESSIONALS
community SITE
stakeholders
landscape architects engineers architects
to see a health care professional may not have an
urban designers
ecologists + biologists
official diagnosis. Lastly, to measure holistic health,
historians
a wide range of professionals in many different
social scientists
disciplines are needed. This complexity may create
economists + statisticians
issues in communication and narrowed views based
public health
on professional specialization. The actor network diagram to the right outlines some of the disciplines that are involved in design, research and health and their relationship to the site and its users.
17
pharmacists + technicians dieticians + nutritionists
geologists + geotechnical
codes and those without insurance or the ability
midwives
client + operations
dentists + hygienists occupational + physical therapists optometrists psychologists + psychiatrists osteopaths, naturopaths + alternative medicine trainers + exercise therapists
Conclusion
Benefits of Predicting and Evaluating Health Outcomes
Issue with Predicting and Evaluating Health Outcomes
Utilizing tools and methods to predict health
While there are many benefits to full project research
outcomes in the design process and evaluate
and evaluation, there are a few dangers to consider.
In conclusion, research can be highly complementary,
results after the project is built can be beneficial
This highly logical and scientific approach to design
however it should enhance and inform design, not
to the project and its players.
Expanding design
may squish creative thinking and cause designers to
narrow its parameters or dictate its form.
thinking into the near and long-term future enriches
only focus on known performance measures, which
quantifiable or even measurable factors such as
the landscape design process and makes the
in turn may smother innovation and cause boring
emotion or creativity should be allowed to coexist
designer feel a sense of accountability.
Metrics
designs. Metrics and tools may cause a designer
alongside logic and science. Research in the design
and evidence-based design processes aim to close
to aim for measurable “points” and forget about
process as well as evaluation of outcomes after
the gap between health issues and what is actually
artful considerations in design, such as emotion,
construction should be conducted in an honest and
being built. Because of its interdisciplinary nature,
experience, or intuition. There is the danger that
transparent way to educate designers, researchers,
a holistic examination of health may facilitate
research may make the design process painful or
health care professionals, clients, stakeholders and
collaboration
unfamiliar
uninspiring. Furthermore, landscapes in particular
users about how the built environment can affect
professionals, fostering information exchange and
are affected by larger regional and global systems,
health. Outcomes should be professionally shared
fresh perspectives.
Integrating research in every
and these “plumes” make it difficult to predict
to expand the already growing body of research
stage of the project synthesizes theory, practice
or determine health outcomes for any given site
in health and the built environment that designers
and research of health and the built environment,
boundary. Lastly, a narrow focus on performance
and decision-makers can learn from. Lastly, funds
which in turn increases the demand for further
outcomes may deduce design to mere numerical or
should be allocated in every public design project
research, builds awareness of the impact the built
financial outcomes, when, in the context of health,
for research for the full life of the project in order
environment has on health, and shifts the baseline
may translate to assigning a number to our wellbeing
to maximize and prioritize understanding health
of what is acceptable to be healthy.
as a race.
outcomes.
between
18
otherwise
Conclusion: A New Approach to Incorporate Complete Health Research
Non-
19
References
Testing the Health Research Process Alberti, M. (January 01, 2005). The Effects of Urban Patterns on Ecosystem Function. International Regional Science Review, 28, 2, 168-192. Anandacoomarasamy, A., Fransen, M., & March, L. (January 01, 2009). Obesity and the musculoskeletal system. Current Opinion in Rheumatology, 21, 1, 71-7. Arnst, C. (August 07, 2006). A SUPERFUND SITE HELPS FIGHT CANCER. Businessweek, 872006, 3996.) Baskin, Y. (November 01, 1994). Ecosystem Function of Biodiversity. Bioscience, 44, 10, 657-660. Bray, G. A. (January 01, 1992). Obesity increases risk for diabetes. International Journal of Obesity and Related Metabolic Disorders : Journal of the International Association for the Study of Obesity, 16, 13-7. Celia, F. (December 01, 2002). DE-STRESS TO DECREASE RISK OF DIABETES. Psychology Today, 35, 6.) Chen, Y., Jiang, Y., & Mao, Y. (January 01, 2009). Association between Obesity and Depression in Canadians. Journal of Women’s Health, 18, 10, 1687-1692. De Sousa, C. (January 01, 2006). Unearthing the benefits of brownfield to green space projects: An examination of project use and quality of life impacts. Local Environment, 11, 5, 577-
20
600. Fitzhugh, E. C., Bassett, D. R., & Evans, M. F. (September 01, 2010). Urban Trails and Physical Activity. American Journal of Preventive Medicine, 39, 3, 259-262. Horwitz, P., & Finlayson, C. M. (January 01, 2011). Wetlands as Settings for Human Health: Incorporating Ecosystem Services and Health Impact Assessment into Water Resource Management. Bioscience, 61, 9, 678-688. Kjellstrom, T., & Weaver, H. J. (January 01, 2009). Climate change and health: impacts, vulnerability, adaptation and mitigation. New South Wales Public Health Bulletin, 20. Kuo, F. E., & Sullivan, W. C. (January 01, 2001). Aggression and Violence in the Inner City: Effects of Environment via Mental Fatigue. Environment and Behavior, 33, 4, 543-571. Lanphear, B. P., Vorhees, C. V., & Bellinger, D. C. (January 01, 2005). Protecting children from environmental toxins. Plos Medicine, 2, 3.) Leyden, K. M. (January 01, 2003). Social capital and the built environment: the importance of walkable neighborhoods. American Journal of Public Health, 93, 9, 1546-51.
Rosner, B., Monson, R. R., Speizer, F. E., ... Hennekens, C. H. (January 01, 1990). A prospective study of obesity and risk of coronary heart disease in women. The New England Journal of Medicine, 322, 13, 882-9. Phibbs, P. (September 01, 1996). News: Birth defects, other disorders linked to Superfund site exposure, ATSDR says. Environmental Science & Technology, 30, 10.) Pope, D. G., & Pope, J. C. (January 01, 2012). Crime and property values: Evidence from the 1990s crime drop.Regional Science and Urban Economics, 42, 177-188. Tompkins, C. L., Soros, A., Sothern, M. S., & Vargas, A. (September 01, 2009). Effects of Physical Activity on Diabetes Management and Lowering Risk for Type 2 Diabetes. American Journal of Health Education, 40, 5, 286-290. Watkins, M. L., Rasmussen, S. A., Honein, M. A., Botto, L. D., & Moore, C. A. (January 01, 2003). Maternal obesity and risk for birth defects. Pediatrics, 111, 5, 1152-8. Yoshida, N., Sugimoto, M., Uchida, T., & Hino, Y. (January 01, 2003). A Study on Psychological Noise Reduction Effects of Roadside Trees in Walking Space. Memoirs- Faculty of Engineering Osaka City University, 44, 59-66.
Lund, H. (May 01, 2003). Pedestrian environments and sense of community. Sage Urban Studies Abstracts: Trends in Urbanization and Urban Society, 31, 2.) Manson, J. E., Colditz, G. A., Stampfer, M. J., Willett, W. C.,
21
AS A RESULT OF HEALTH EVALUATION
ADAPTIVE INTERVENTIONS
01
AS A RESULT OF HEALTH EVALUATION
ADAPTIVE INTERVENTIONS
Introduction
Adaptive Interventions
“It is no measure of health to be well adjusted to a profoundly sick society.� ~Jiddu Krishnamurti
Common contemporary practices rarely incorporate
Using the DIG Studio project as an example design
long-term
management
that would benefit from long term evaluation, this
strategy, and even more rarely do projects examine
section identifies a need for adaptive management
long term health impacts. This lack of evaluation
practices to direct physical outcomes that will
and understanding of design results over time may
maximize health outcomes.
monitoring
into
the
How might the health dialogue continue
reduce health potentials or even create unhealthy results.
Long term monitoring may continue the
The
following
pages
explore
how
adaptive
health dialogue and provide a better understanding
interventions could be utilized to steer a project
of the long-term health implications of design
towards previously established health outcomes.
interventions.
Due to time constraints and a theoretical test project,
through
long-term
evaluation
insertions of adaptive interventions?
adaptive intervention techniques were not able to be This section explores how long term monitoring
tested directly on the DIG Studio project, however
can be incorporated into a project to determine
a system for how interventions could be inserted is
success.
discussed. This section asks the question:
Success is established by a variety of
factors and includes success in the process and acknowledgement of health as well as the actual health outcome.
02
informing
03
According to the Minnesota Dept. of Health there
What is Success?
are several different types of evaluation. These are:
Evaluation occurs so the designer, client or researcher can determine how successful the project is and identify any changes needed to be made to increase success. This begs the following questions: What does one evaluate when determining success? How does one know if a strategy is successful?
In their book The Effectiveness of Health Impact
This is important in understanding the varying
Assessment, Wismar, Blau, Ernst and Figueras
degrees of how a health framework in design might
explain that there are varying degrees of health
begin to be evaluated.
implementing the health intervention
effectiveness when it comes to decision making,
doesn’t change design decisions at first, the process
Application: What was accomplished by incorporating
balancing education and acknowledgement with
of implementing the framework could spur dialogue
health and research into the design process?
actual actions taken. These degrees are summarized
and awareness of health implications of design,
in the chart to the right. An intervention is deemed
potentially informing the next project and set of
Impact
“effective” if health is acknowledged and a decision
design decisions. It could be argued that designers
-evaluating how well the goals were reached
was changed in support of health.
If no change
might already be subconsciously making design
Application: Was health more understood? How did
was made in the decision, but health was added to
decisions that positively affect health, they just
the health framework affect the design outcome?
the dialogue among decision makers, the authors
might not be understand the health outcomes or the
say they “raised awareness” of health, a success
magnitude of this impact. The degrees of health
Outcome
in itself. If a decision was changed but health was
effectiveness tell us that an understanding of health
-evaluating the health results
not the basis for that change, the authors label
is just as important, because without this education,
Application: How did the health-design process or
it “opportunistic,” pointing out that it is not full
health outcomes will not achieve their full potential.
the designed landscape affect long-term health?
success unless there is a genuine understanding
Process -evaluating
the
methods
and
process
for
Even if the framework
of the action taken. Lastly, if health never entered Summative
the discussion and no decisions were changed, the
-A combination of measurements and judgements
intervention was not deemed successful (Wismar et
about the process, impact and outcome that
al., 2007).
determines the overall success of the action Application: What is the overall success of these new approaches that integrate health and design? 04
05
Degrees of Health Effectiveness HEALTH ACKNOWLEDGED
Measuring Success
+
+
-
effective
raised awareness
-
opportunistic
ignored, rejected
DECISION CHANGED
[modified from Wismar et al., 2007, p 22]
set minimal parameters for health, while personal
Parameters for Success
opinions of health and wellbeing might reach for a Diagram of Health Parameters
Individual health outcomes can be measured and
sibl
}
determine the amount of success. Parameters can be set based on goals established by stakeholders in the beginning of the project. They can be crosschecked with predicted health outcomes that emerge from the evidence-based design process and regulatory standards that apply to the site. Parameters should be revisited over time to reflect a changing community and their needs. To some degree, it is easier to determine health failure over health success.
The diagram to the
right describes the clarity of un-health as being worse than the existing state. The “do no harm” point is maintaining the existing state.
Health
and wellness, however have varying degrees of success.
With each
health “bracket” follows a
different health resultant. Health and wellbeing can almost always be reevaluated to reach for a higher
higher standard.
pos
evaluated only after parameters are established to
} }} {{ {
o do n harm
ealth
un-h
}}}{{{ }{
i
eas
incr
lth +
ea ng h
we
ss llne
incr
eas
ing
hea
lth +
wel
lnes
s
e re
sult
{
do n har o m
ants
07
06
UNHEALTH ADAPTIVE INTERVENTION
After parameters are established to determine what is deemed unsuccessful, or unhealthy, monitoring and evaluation can occur to measure success. Monitoring ideally should occur periodically and over a long period of time to determine long-term health
M
O HAR
DO N
successes. If monitoring results deem an aspect of the project and its health outcome unsuccessful, then the client, designer or site manager should intervene with a design intervention or policy to fix the issue.
INITIAL DESIGN INTERVENTION
HEALTH SUCCESS
This practice of allowing flexibility
INCREASING HEALTH + WELLBEING
and growth in design, monitoring periodically, and intervening when necessary is called adaptive
DO N
O HA
management. Adaptive management is a growing
RM
trend, especially in ecological design, allowing for several acceptable design results instead of a static masterplan as a goal. If the design strays outside the health parameters, adaptive interventions can
un-
hea
lth
be utilized to steer the outcome back on the track to success. The diagram to the right illustrates this
standard. Additionally, regulatory standards might
Diagram of the Role of Adaptive Interventions To Steer Towards Acceptable Health Parameters
concept.
UNHEALTH TIME
07
Conclusion
Testing the Adaptive Intervention Process
A New Approach: Adaptive Interventions To Increase Health
In the interest of time, DIG Studio was not able to
In sum, adaptive interventions may be an effective
establish specific parameters for each predicted
way to aim for successful health outcomes over time
health outcome, and because it is a theoretical
and maximize the health of people, landscapes and
project, it is not feasible to test the implementation
ecologies. The findings in the previous pages may
of adaptive management. That said, the adaptive
identify a need for:
References
Measuring Success Minnesota Department of Health. (2012, May). Types of health evaluation. Retrieved from http://www.health.state. mn.us/divs/hpcd/chp/hpkit/text/eval_types.htm Wismar M, Blau J, Ernst K, Figueras J. The effectiveness of health impact assessment: Scope and limitations of supporting decision-making in Europe. Brussels: European Observatory on Health Systems and Policies, 2007.
management process would be quite appropriate for this project. Because health is the goal, rather than
•
a static masterplan or specific physical outcome, ongoing evaluation will be necessary to determine
Defined health parameters to guide health evaluation
•
Ongoing dialogue and evaluation with client,
the successes of the project. Adaptive interventions
community, and users for periodic reexamination
will steer the physical outcomes when they begin to
of health standards
•
drift off course.
Periodic evaluation over the long-term for checkpoints on health status over time
•
Adaptive management strategies for projects involving health to intervene when outcomes steer outside the health parameters
By establishing a methodology and prioritizing funding for adaptive interventions, the health dialogue can continue, maximizing potential health outcomes. 08
09
END SCRIPT
1
Three major ideas informed DIG Studio: Indeterminacy, landscape urbanism and toxicity: (i)
Structure
Indeterminacy implies process-based design based on adaptive
cycles, maintenance regimes, and entropy. Our understanding is rooted as much in resilience thinking as it is in Dadaist art: indeterminacy was always challenged by the relevance of site components and archeology, such as buried pilings or disused railroad tracks.
(ii)
Landscape urbanism factored in as a contemporary theoretical
body of knowledge and influence, both in its successes and its failures. Major projects such as Downsview, Fresh Kills, as well as the theory surrounding such projects had a major influence: there was always a tension between the exact scale of landscape (e.g. the Columbia River Basin) and the somatic experience of walking along the Willamette River’s armored banks.
(iii)
Toxicity manifested throughout the project as the plume—
the revealer of arbitrary geographies of property and jurisdiction. A resultant of innumerable factors, both natural and anthropogenic: toxicity was magnified as the language of the plume was incorporated into the drawings, both structurally and thematically. These three ideas coalesced in Dig Studio’s effort convey complex ideas about time and its unknown effect via a visual language. Landscape architecture is broadly about both space and time, but even when a project has considered and incorporated future projections (which every project that shows full grown trees in their plans has done), the work doesn’t necessarily visually describe the nature of time and the speculations inherent in every project.
Dig Studio’s groundwork investigations
examined the speculative nature of designing for the future as well as how one might properly convey that speculation.
Ultimately, Dig Studio’s graphical notations sought to describe sets of divergent occurrences and cinematic mutations of space (physical and
Representation
aural) with time signatures and script insertions. The graphic notations and networks were an ever evolving language, developed to illustrate temporal processes and the varied trajectories that a design might take based on insertions in/onto specific site surfaces, geology and ecologies. This language was continually developed and refined during the design process. The site plan for McCormick & Baxter was largely a graphic problem about how to properly convey various and tangled future trajectories that result from an initial set of insertions without appearing overly prescriptive.
02
03
The incorporation of health, after the mid-term, had a crystallizing effect on Dig’s process. Certain trajectories became imperative, while others
Outcomes
were de-emphasized. Representation remained subject to projection systems, long-phase feedback loops, and process-based design. The extent of representation that we explored was curtailed by the struggle to operationalize an indeterminate-outcome based design process. External collaborations with parallel thesis efforts coalesced into a broader, more structurally significant body of work. The degree of indeterminacy was not only thematic, but also structural. That is to say, many outcomes were conceived, many manifestations discussed. Each would have been different, but equally valid. From the selection of the Port of Portland Superfund Site to the decision to focus on McCormic & Baxter and Triangle Park at a higher resolution were all discussed at length, with multiple fluctuations in stance and opinion. DIG generated its own degree of internal tensions between working preferences, tactics, and strategies. However, the graphical resolutions and conventions were easily established, resulting in a graphical alloy—drawings that embody the effort and ideas of multiple authors collaborating across multiple platforms to communicate one idea at a multitude of scales.
The work of DIG STUDIO suggests several trajectories for further development and investigation. Among these would be a further develop-
Trajectories
ment of graphical resolution in both plan and section, as well as in the script archive. Exploding the script archive into subsets and multiple deployment variants would also lead to a higher resolution reading of many of the embodied mechanisms and tropes within the scripts, and especially how they might relate to particular landscape conditions. For such a task, further study of interpretive scores written by composers/ artists such as Stockhausen, George Crumb and John Cage would prove an essential starting point. Another trajectory is the development of a construction drawing set annotated with speculative temporal notations regarding probable future configurations. A construction set would be a particularly intriguing place to combine the specificity of the initial script insertions, their construction, and the indeterminacy of future outcomes. A third trajectory would be the incorporation of graphical metrics that would be used in the validation or monitoring of indeterminate site-based processes.
04
05
THE PERSON IT POINTS TO IS THE AUTHOR
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The following is a table containing the contaminants that are found on every superfund site within the Portland indutrial district. The table is organized by the owner of each site as well as numbers that reference
Chemical Index
Contamination by owner
CHEMICAL INDEX
Appendix A
the index map that can be found in the REGIONAL ANALYSIS booklet.
02
03
2
Terminal 5
CHROMIUM
METAL
MERCURY
METAL
2
Terminal 6
CHROMIUM
METAL
PAH
HYDROCARBON
2
Terminal 7
PCB
ORGANOCHLORIDE
TRIBUTYLTIN
TBT
3
Oregon Steel Mill
CADMIUM
METAL
ZINC
METAL
CHROMIUM
METAL
BENZENE
BTEX
COPPER
METAL
BUTYLBENZENE,
HYDROCARBON
HPAH
HYDROCARBON
CHLOROETHANE
AOC
LEAD
METAL
DICHLOROETHANE,1,1
AOC
LPAH
HYDROCARBON
DIESEL - FUEL OI
HYDROCARBON
PAH
HYDROCARBON
ETHYLBENZENE
BTEX
PCB
ORGANOCHLORIDE
GASOLINE
HYDROCARBON
TPH
HYDROCARBON
NAPHTHALEN
BTEX
ZINC
METAL
PROPYLBENZENE
HYDROCARBON
STYRENE
BTEX
7
Premier Edible Oils
4
Consolidated MetCc
TPH
HYDROCARBON
5
Time Oil Co.
BENZO(a)PYRENE
HYDROCARBON
CHRYSENE
HYDROCARBON
TRICHLOROETHANE,1,1,
CHLORINATED HYDROCARBON
LEAD
METAL
TRIMETHYLBENZENE,1,3,5
BTEX
NAPHTHALENE
BTEX
XYLENE
BTEX
PCB
ORGANOCHLORIDE
ANTIMONY
METAL
DIBENZOFURAN
HOC
PENTACHLOROPHENOL
CHLORINATED HYDROCARBON
HPAH
HYDROCARBON
THC
HYDROCARBON
ANTIMONY
METAL
LPAH
HYDROCARBON
DIBENZOFURAN
HOC
MERCURY
METAL
HPAH
HYDROCARBON
PAH
HYDROCARBON
TRIBUTYLTIN
TBT
6
RoMar Realty
02
8
Jefferson Smurfit
03
9
Schnitzer Steel
DICHLOROETHANE,1,1
AOC
METAL
PAH
HYDROCARBON
ANTIMONY
METAL
PCB
ORGANOCHLORIDE
ARSENIC
METAL
ZINC
METAL
ALUMINUM
10
NW PIPE
TETRACHLOROETHYLENE
BTEX
12
Terminal 4 Slip 1
CADMIUM
METAL
BIS(2-ETHYLHEXYL)PHTHALAT HYDROCARBON
12
Terminal 4 Slip 2
CHROMIUM
METAL
12
Terminal 4 Slip 3
DDT
ORGANOCHLORIDE
BUTYL BENZYL PHTHALATE
HYDROCARBON
12
Terminal 4 Slip 4
LEAD
METAL
CADMIUM
METAL
12
Terminal 4 Slip 5
ZINC
METAL
CARBAZOLE
AHOC
13
Terminal 4 Slip 10
CHROMIUM
METAL
CHROMIUM
METAL
13
Terminal 4 Slip 11
CHRYSENE
HYDROCARBON
COBALT
METAL
13
Terminal 4 Slip 12
DDD,p,p’-
ORGANOCHLORIDE
COPPER
METAL
13
Terminal 4 Slip 13
DIBENZO(a,h)ANTHRACENE
HYDROCARBON
DIBENZOFURAN
HOC
13
Terminal 4 Slip 14
DIESEL - FUEL OIL
HYDROCARBON
HPAH
HYDROCARBON
13
Terminal 4 Slip 15
FLUORANTHENE
PAH
13
Terminal 4 Slip 16
FLUORENE
PAH
IRON
METAL
13
Terminal 4 Slip 17
INDENO(1,2,3-cd)PYRENE
PAH
LEAD
METAL
13
Terminal 4 Slip 18
LEAD
METAL
LPAH
HYDROCARBON
13
Terminal 4 Slip 19
MERCURY
METAL
MERCURY
METAL
13
Terminal 4 Slip 20
NAPHTHALENE
BTEX
13
Terminal 4 Slip 3
ACENAPHTHENE
HYDROCARBON
METHYLNAPHTHALENE,
CHLORINATED HYDROCARBON
ANTHRACENE
HYDROCARBON
NICKEL
METAL
13
Terminal 4 Slip 4
ANTIMONY
METAL
PAH
HYDROCARBON
13
Terminal 4 Slip 5
BENZO(a)ANTHRACENE
HYDROCARBON
SILVER
METAL
13
Terminal 4 Slip 6
BENZO(b)FLUORANTHENE
HYDROCARBON
ZINC
METAL
13
Terminal 4 Slip 7
BENZO(ghi)PERYLENE
HYDROCARBON
BARIUM
METAL
04
05
13
Terminal 4 Slip 8
BENZO(k)FLUORANTHENE
HYDROCARBON
LEAD
METAL
13
Terminal 4 Slip 9
CADMIUM
METAL
MERCURY
METAL
14
St. Johns Tank Farm
BENZO(a)PYRENE
HYDROCARBON
NICKEL
METAL
LEAD
METAL
OIL
HYDROCARBON
PAH
HYDROCARBON
PCB
ORGANOCHLORIDE
TETRACHLOROETHYLENE
BTEX
TRIBUTYLTIN
TBT
ZINC
METAL
15
16
17
18
19
Terminal 4-Auto Storage ARSENIC
Mar Com Inc.NORTH
Mar Com Inc. SOUTH
Crawford Street Co.
Willamette Cove
METAL
LEAD
METAL
PAH
HYDROCARBON
TPH
HYDROCARBON
COPPER
METAL
OIL TRIIBUTYLTIN
20
McCormick & Baxter Creosoting Co.
ARSENIC
METAL
HYDROCARBON
CHROMIUM
METAL
TBT
COPPER
METAL
ZINC
METAL
PAH
HYDROCARBON
COPPER
METAL PENTACHLOROPHENOL
CHLORINATED HYDROCARBON
ACENAPHTHENE
HYDROCARBON
ANTHRACENE
HYDROCARBON
ANTIMONY
METAL
ARSENIC
METAL
BENZENE
BTEX
BENZO(a)ANTHRACENE
HYDROCARBON
BENZO(a)PYRENE
HYDROCARBON
BENZO(b)FLUORANTHEN
HYDROCARBON
BERYLLIUM
METAL
CADMIUM
METAL
OIL
HYDROCARBON
TRIIBUTYLTIN
TBT
ZINC
METAL
DI-n-BUTYL PHTHALATE
PHTHALATE
LEAD
METAL
MERCURY
METAL
TRIBUTYLTIN
TBT
ARSENIC
METAL
CADMIUM
METAL
CHROMIUM
METAL
COPPER
METAL
06
21
Triangle Park
07
TETRACHLOROBENZENE,1,2,4,5-
BTEX
TETRACHLOROETHYLENE
BTEX
TOLUENE
BTEX
TRIBUTYLTIN
TBT
DICHLOROETHYLENE,1,2-CIS- AOC
TRICHLOROETHANE,1,1,1-
CHLORINATED HYDROCARBON
DICHLOROPROPANE,1,2-
AOC
TRIMETHYLBENZENE,1,2,4-
BTEX
DIESEL - FUEL OIL
HYDROCARBON
TRIMETHYLBENZENE,1,3,5-
BTEX
DI-n-BUTYL PHTHALATE
PHTHALATE
FLUORANTHENE
PAH
VINYL CHLORIDE
CHLORINATED HYDROCARBON
FLUORENE
PAH
XYLENE
BTEX
GASOLINE
HYDROCARBON
ZINC
METAL
INDENO(1,2,3-cd)PYRENE
PAH
LPAH
HYDROCARBON
ISOPROPYLTOLUENE,p-
BTEX
MERCURY
METAL
LEAD
METAL
PAH
HYDROCARBON
METHYLENE CHLORIDE
CHLORINATED HYDROCARBON
NAPHTHALENE
BTEX
NICKEL
METAL
OIL - LUBRICATING
HYDROCARBON
PCBs
ORGANOCHLORIDE
COPPER
METAL
PENTACHLOROBENZENE
CHLORINATED HYDROCARBON
HPAH
HYDROCARBON
PHENANTHRENE
PAH
PAH
HYDROCARBON
PYRENE
PAH
ZINC
METAL
CHROMIUM
METAL
CHRYSENE
HYDROCARBON
COPPER
METAL
DIBENZO(a,h)ANTHRACENE
HYDROCARBON
DICHLOROETHANE,1,1-
AOC
08
22
23
24
US COAST GUARD
Freightliner - Truck Manuf BIS(2-ETHYLHEXYL)PHTHALPlant ATE HYDROCARBON
Fred Devine Diving and Salvage Co
COPPER
METAL
CRESOL,4
PHENOL
ARSENIC
METAL
09
25
26
Swan Island Portland Ship Yard
27
ARSENIC
UPRR - Albina Yard
METAL
ARSENIC
METAL
BENZO(a)ANTHRACENE
HYDROCARBON
BIS(2-ETHYLHEXYL)PHTHALATE HYDROCARBON
BENZO(a)PYRENE
HYDROCARBON
BUTYL BENZYL PHTHALATE
HYDROCARBON
BENZO(b)FLUORANTHENE
HYDROCARBON
CHROMIUM
METAL
CADMIUM
METAL
DI-n-OCTYL PHTHALATE
PHTHALATE
CHROMIUM
METAL
LEAD
METAL
CHRYSENE
HYDROCARBON
PAH
HYDROCARBON
COPPER
METAL
ZINC
METAL
FLUORANTHENE
PAH
INDENO(1,2,3-cd)PYRENE
PAH
LEAD
METAL
MERCURY
METAL
PAH
HYDROCARBON
PCB
ORGANOCHLORIDE
PHENANTHRENE PYRENE
29
Port of Portland - Terminal 1 South ARSENIC
METAL
LEAD
METAL
PAH
HYDROCARBON
TPH
HYDROCARBON
Port of Portland - Terminal 1 North ARSENIC
METAL
PAH
COPPER
METAL
30
PAH
LEAD
METAL
TRIBUTYLTIN
TBT
OIL
HYDROCARBON
TRICHLOROETHYLENE
CHLORINATED HYDROCARBON
PAH
HYDROCARBON
ZINC
METAL
Goldendale Aluminum Co ARSENIC
METAL
BIS(2-ETHYLHEXYL)PHTHALAT HYDROCARBON
31
PGE - Station E
32
Sulzer Bingham Pumps BENZENE
GASOLINE
HYDROCARBON BTEX
DICHLOROETHYL
AOC
FUEL OIL
HYDROCARBON
LEAD
METAL
TETRACHLOROETHYLENE
BTEX
ZINC
METAL
TOLUENE
BTEX
10
11
34
36
37
Galvanizers Co.
Gunderson Inc.
TRICHLOROETHYLENE
CHLORINATED HYDROCARBON
BENZO(a)PYRENE S
HYDROCARBON
BENZO(b)FLUORANTHENE
HYDROCARBON
VINYL CHLORIDE
CHLORINATED HYDROCARBON
BENZO(ghi)PERYLENE
HYDROCARBON HYDROCARBON
XYLENE
BTEX
BENZO(k)FLUORANTHENE
CHROMIUM
METAL
CHRYSENE
HYDROCARBON
IRON
METAL
DIBENZO(a,h)ANTHRACENE
HYDROCARBON
LEAD
METAL
ETHYLBENZENE
BTEX
PAH
HYDROCARBON
FLUORANTHENE
PAH
ZINC
METAL
FLUORENE
PAH
CADMIUM
METAL
INDENO(1,2,3-cd)PYRENE
PAH
CHROMIUM
METAL
LEAD
METAL
COPPER
METAL
NAPHTHALENE
BTEX
DICHLOROETHYLENE,1,1-
AOC
PHENANTHRENE
PAH
LEAD
METAL
PYRENE
PAH
MERCURY
METAL
TOLUENE
BTEX
TETRACHLOROETHYLENE
BTEX
TPH
HYDROCARBON
TPH
HYDROCARBON
XYLENE
BTEX
TRICHLOROETHANE,1,1,1-
CHLORINATED HYDROCARBON
ANTIMONY
METAL
ZINC
METAL
BARIUM
METAL
BENZOIC ACID
HYDROCARBON
CADMIUM
METAL
CRESOL,4
PHENOL
LEAD
METAL
MERCURY
METAL
Texaco Portland Terminal ACENAPHTHENE
HYDROCARBON
ANTHRACENE
HYDROCARBON
ARSENIC
METAL
BENZENE
BTEX
BENZO(a)ANTHRACENE
HYDROCARBON
12
38
lakeside Industries
13
SILVER 39
40
41
CALBAG METALS
SHAVER TRANSPORTATION
SCHNITZER KITTRIDGE
METAL
TPH
HYDROCARBON
ZINC
METAL
ANTIMONY
METAL
ZINC
METAL
ANTIMONY
METAL
BARIUM
METAL
BARIUM
METAL
BENZOIC ACID
HYDROCARBON
BENZOIC ACID
HYDROCARBON
CADMIUM
METAL
CRESOL,4-
PHENOL
LEAD
METAL
LEAD
METAL
MERCURY
METAL
MERCURY
METAL
SILVER
METAL
SILVER
METAL
ZINC
METAL
THALLIUM
METAL
CADMIUM
METAL
ZINC
METAL
ACENAPHTHYLENE
HYDROCARBON
COPPER
METAL
ARSENIC
METAL
LEAD
METAL
BARIUM
METAL
MERCURY
METAL
BENZENE
BTEX
ZINC
METAL
ACETONE
HYDROCARBON
BENZO(a)ANTHRACENE
HYDROCARBON
BENZO(a)PYRENE
HYDROCARBON
BENZO(b)FLUORANTHENE
HYDROCARBON
CHRYSENE
HYDROCARBON
DIESEL - FU
HYDROCARBON
NAPHTHALENE
BTEX
PHENOLS
PHENOL
TOLUENE
BTEX
TPH
HYDROCARBON
ACETONE ARSENIC
METAL
CADMIUM
METAL
LEAD
METAL
MERCURY
METAL
METHYL-2-PENTANONE,4-
CHLORINATED HYDROCARBON
PCBs
ORGANOCHLORIDE
14
42
44
FRONT LP
CHEVRON ASPHALT
15
VANDIUM 45
46
47
McCall Oil
METAL GOULD ELECTRONIC
TPH
HYDROCARBON
ARSENIC
METAL
XYLENE
BTEX
ALUMINUM
METAL
CADMIUM
METAL
BARIUM
METAL
LEAD
METAL
BUNKER - FUEL OIL
HYDROCARBON
SULFURIC ACID
MINERAL ACID
BUTYL BENZYL PHTHALATE
HYDROCARBON
ZINC
METAL
BENZENE
BTEX
D,2,4
PHENOXY HERBICIDE
DB,2,4
PHENOXY HERBICIDE
DICHLOROBENZENE1,2
AOC
DICHLOROPHENOL,2,4
AOC
DICHLOROPHENOL,2,6
AOC
DICHLOROPROPANE,1,2-
AOC
ETHYLBENZENE
BTEX
MCPA
PHENOL
CADMIUM
METAL
CRESOL,4-
PHENOL
DIBENZOFURAN
HOC
DI-n-OCTYL PHTHALATE
PHTHALATE
LEAD
METAL
MERCURY
METAL
PAH
HYDROCARBON
ZINC
METAL
WILLBRIDGE TERMINAL ARSENIC
GS ROOFING
48
METAL
49
Rhone-Poulenc - Doane Lake
BENZENE
BTEX
BENZO(a)PYRENE
HYDROCARBON
METHYLENE CHLORIDE
CHLORINATED HYDROCARBON
CHROMIUM
METAL
PHENOLS
PHENOL
ETHYLBENZENE
BTEX
T,2,4,5
AUXIN
LEAD
METAL
MERCURY
METAL
TETRACHLORODIBENZO-pDIOXIN
BTEX
NAPHTHALENE
BTEX
TOULENE
BTEX
BENZENE
BTEX
TRICHLOROETHYLENE
CHLORINATED HYDROCARBON
BUNKER - FUEL OIL
HYDROCARBON
TRICHLOROPHENOL,2,4,,5
PHENOL
16
17
XYLENE 50
51
ARKEMA
SILTRONIC
BTEX
AMMONIA
IRON
METAL
MAGANESE
METAL
MANGANESE
METAL
METHYLNAPHTHALENE,2
CHLORINATED HYDROCARBON
PAH
HYDROCARBON
CHLOROBENZENE
AOC
CHROMIUM
METAL
DDT
ORGANOCHLORIDE
SODIUM BICHROMATE
METAL
BENZENE
BTEX
PENTACHLOROPHENOL
CHLORINATED HYDROCARBON
BENZO(a)ANTHRACENE
HYDROCARBON
SELENIUM
METAL
BENZO(b)FLUORANTHENE
HYDROCARBON
SELENIUM
METAL
BERYLLIUM
METAL
SILVER
METAL
SILVER
METAL
TETRACHLOROETHYLENE
BTEX
TITANIUM
METAL
TITANIUM
METAL
TOLUENE
BTEX
TOLUENEDIAMINE,2,4
AMINE
VANADIUM
METAL
VANADIUM
METAL
ZINC
METAL
ZINC
METAL
BENZENE
BTEX
CYANIDE (AS ION)
NITRILE
NAPHTHALENE
BTEX
PAH
HYDROCARBON
BIS(2-ETHYLHEXYL)PHTHALATE HYDROCARBON CARBAZOLE
AHOC
CHLOROPHENOL
ORGANOCHLORIDE
CHRYSENE
HYDROCARBON
COBALT
METAL
COBALT
METAL
D,2,4-
PHENOXY HERBICIDE
DDT
ORGANOCHLORIDE
DIBENZOFURAN
HOC
DIMETHYLPHENOL,2,4
PHENOL
DI-n-BUTYL PHTHALATE
PHTHALATE
ETHYLBENZENE
BTEX
INDENO(1,2,3-cd)PYRENE
PAH
IRON
METAL
18
52
NW GASCO
19
53
UW MOORINGS
ACENAPHTHENE ANTHRACENE
HYDROCARBON
ARSENIC
METAL 54
MARINE FINANCE
PYRENE
PAH
TRIBUTYLTIN
TBT
ZINC
METAL
ARSENIC
METAL
BENZO(a)ANTHRACENE
HYDROCARBON
BENZO(a)PYRENE
HYDROCARBON
BENZO(a)PYRENE
HYDROCARBON
BENZO(b)FLUORANTHENE
HYDROCARBON
CARBAZOLE
AHOC
BENZO(ghi)PERYLENE
HYDROCARBON
CHROMIUM
METAL
CHROMIUM
METAL
CHRYSENE
HYDROCARBON
CHRYSENE
HYDROCARBON
COPPER
METAL
COPPER
METAL
DIBENZOFURAN
HOC
DDD,p,p’-
ORGANOCHLORIDE
DIBENZOFURAN S
HOC
DDT,p,p’-
ORGANOCHLORIDE
INDENO(1,2,3-cd)PYRENE
PAH
DIBENZO(a,h)ANTHRACENE
HYDROCARBON
LEAD
METAL
DIBENZOFURAN
HOC
CHLORINATED HYDROCARBON
DIELDRIN
CHLORINATED HYDROCARBON
METHYLNAPHTHALENE,2PAH
HYDROCARBON
FLUORANTHENE
PAH
ZINC
METAL
FLUORENE
PAH
BENZENE
BTEX
INDENO(1,2,3-cd)PYRENE
PAH
BUTYL BENZYL PHTHALATE
HYDROCARBON
LEAD
METAL
NAPHTHALENE
BTEX
NAPHTHALENE
BTEX
PAH
HYDROCARBON
PAH
HYDROCARBON
TPH
HYDROCARBON
PCBs
ORGANOCHLORIDE
TRIMETHYLBENZENE,1,2,4-
BTEX
PHENANTHRENE
PAH
XYLENE
BTEX
BENZENE
BTEX
55
56
20
BRIX/ FOSS MARITIME
NU STAR
21
BUTYL BENZYL PHTHALATE
HYDROCARBON
DICHLOROBENZENE, 1,2
AOC
ETHYLBENZENE
BTEX
DICHLOROBENZENE, 1,3
AOC
GASOLINE
HYDROCARBON
DICHLOROBENZENE, 1,4
AOC
PAH
HYDROCARBON
DIESEL
HYDROCARBON
THALLIUM
METAL
ETHYLBENZENE
BTEX
TOLUENE
BTEX
FLUORANTHENE
PAH
XYLENE
BTEX
FLUORENE
PAH
57
EXXON-MOBIL
DIESEL
HYDROCARBON
GASOLINE
HYDROCARBON
58
ARCO/ BP TERMINAL
DIESEL
HYDROCARBON
INDENO(1,2,3-cd)PYRENE
PAH
GASOLINE
HYDROCARBON METHYLNAPHTHALENE,2-
CHLORINATED HYDROCARBON
METHYL-tert-BUTYL ETHER
CHLORINATED HYDROCARBON
NAPHTHALENE
BTEX
PAH
HYDROCARBON
PHENANTHRENE
PAH
PYRENE
PAH
THALLIUM
METAL
TOULENE
BTEX
TPH
HYDROCARBON
XYLENE
BTEX
60
Kinder Morgan Liquid
LEAD
METAL
PAH
HYDROCARBON
ACENAPHTHENE
HYDROCARBON
ANTHRACENE
HYDROCARBON
BARIUM
METAL
BENZO(a)ANTHRACENE
HYDROCARBON
BENZO(a)PYRENE
HYDROCARBON
BENZO(b)FLUORANTHENE
HYDROCARBON
BIS(2-ETHYLHEXYL)PHTHALATE HYDROCARBON CHLOROBENZENE
AOC
CHRYSENE
HYDROCARBON
CRESOL,4-
PHENOL
DIBENZO(a,h)ANTHRACENE
HYDROCARBON
DIBENZOFURAN
HOC
22
61
Owens Corning fiberglass ARSENIC
METAL
CHROMIUM
METAL
COPPER
METAL
PAH
HYDROCARBON
23
PENTACHLOROPHENOL
CHLORINATED HYDROCARBON
62
ACF INDUSTRIES
TPH
HYDROCARBON
63
GP- Linnton Fiber Terminal
PAH
HYDROCARBON
64
Linnton Oil Fire Training
ACENAPHTHENE
65
ANTHRACENE
HYDROCARBON
ARSENIC
METAL
BENZENE
BTEX
BENZO(a)ANTHRACENE
HYDROCARBON
BENZO(a)PYRENE
HYDROCARBON
CHRYSENE
HYDROCARBON
DICHLOROETHANE,1,1-
AOC
DICHLOROETHYLENE,1,1-
AOC
ETHYLBENZENE
BTEX
FLUORANTHENE
PAH
FLUORENE
PAH
NAPHTHALENE
BTEX
PHENANTHRENE
PAH
PYRENE
PAH
TOLUENE
BTEX
TRICHLOROETHANE,1,1,1-
CHLORINATED HYDROCARBON
XYLENE
BTEX
PGE - Harborton Substation DIURON
PAH
HYDROCARBON
PCBs
ORGANOCHLORIDE
TPH
HYDROCARBON
HERBICIDE
24
25