Dig la (2)

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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.

04

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

08

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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the Alternative of Hermeneutics. Landscape

BASF, (2005c). New Forms of High-pressure Synthesis. BASF Historical Milestones 1865-

Bois, Y.A., and Krauss, R.E., ed, (1997).

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Baker, J., et al (2004). Alternative Futures for

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world’s ecosystem services and natural capital.

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Corner, J., and MacLean, S., (2000). Taking

Economics 63, pps 616-626.

Measures Across the American Landscape. Yale

Czerniak, J., (2002). Looking Back at Landscape

University Press,

Urbansim: Speculations on Site. Ecology and

Design: Frameworks For Learning. Island Press.

Brand, F.S. and Jax, K., (2007). Focusing

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Jrnl. Fall 1991 vol. 10 no. 2 115-133

the Meaning(s) of Resilience: Resilience as a

Corner, J. (1999). Eidetic Operations and New

Bélanger, P., (2009). Landscape as

Descriptive Concept and a Boundary Object.

Landscapes. Recovering Landscape: Essays

Czerniak, J., and Hargreaves, G., (2007). Large

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.

24

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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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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

25


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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03


R ZE IT HN SC

LA

IL

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FO

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T ET M

RK PA

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.

I SK E OR DM

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UF

BL F

4

TE

RK

PA

ET M

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AL IN RM

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TRANSECT 4

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E BL UF FS

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PA

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LA

AR

ST

&

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1:12500

TRANSECT 3

FS UF

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1:12500

TRANSECT 2 1:12500

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TRANSECT 1

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TOPO

1:12500

04

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,

n>

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

n>

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

n>

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

n>

RAIL

meaningful way.

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15


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

n>

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.

58 57

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

24

n>

[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

44 41

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

e re

ants

} { } }} {{{ }{

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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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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


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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


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