Update 11 :: Frost 2022

This is a different kind of update. There is no play-by-play description of activites. Instead here is a snapshot of the emerging system that I have been working on. Heretofore its mostly been in pieces, only part of a living whole in my imagination. Lets see if I can lay it out in brief terms:

I’d like us to invent a bioregional network, capable of doing work together, while minimizing dependencies on hierarchical institutions or industrial currency.

I suspect that to restore our bioregion will require a self-replicating swarm of skilled people to start tending “public trust landscapes”. Public Trust Landscapes are the web of forests, soils, wetlands and streams which creates ecological functions that are shared by all and are held in trust for our children: water quantity, water quality, flood storage, biodiversity, carbon storage, agricultural production capacity, and fish and wildlife populations. Private landowners when left isolated in global markets, have proven to degrade neglect these public trust functions.

We need to rebuild a cultural foundation for stewardship. By working, eating, and telling stories around a fire in cultivated semi-wild forest gardens we grow new relationships among people and with the earth, and are happier. By cultivating our needs locally we reduce our dependency on global colonial-industrial systems and thereby reduce harm, and create new opportunities. Bioregional regeneration is tangible work. Wetlands, streams, rivers and floodplains have been damaged and neglected. If bioregionalism doesn’t naturally tend land through cultural processes, without being instructed to do so by institutions or only when seeking personal income, it reeks of fakery. Landscape regeneration and stewardship must be a lifestyle choice.

Here is my hypothetical model, corresponding with the diagram above, with key elements from the diagram capitalized in text: BIOCULTURAL RESTORATION FIELD STATIONS are the place where LOCAL BIOREGIONAL GROUPS can congregate to tend patches of vegetation. Patches of vegetation make up woods and wetlands, and woods and wetlands make up landscapes. To arrive at any site and work comfortably using local energy sources, we develop FIELD STATION INFRASTRUCTURE–a tool kit of appropriate technology that conveniently also provides education about how to live sustainably, as well as disaster resilience. While stepping away, and living at a field station we are momentarily carbon positive, restoring ecosystems, and among colleagues, close to nature.

SPRING DESIGN CHARRETTES are annual gatherings hosted by a field station where we redesign specific ecosystem patches. These designs inform our work in the landscapes around field stations. These collaborative and iterative design efforts both depends on and generate NATIVE AGROFORESTRY DESIGN RESOURCES–the lists and practices and patterns that inform how we semi-wild vegetation. We can collectively store and retrieve these resources on the SALISH SEA WIKI.

By doing good work, field stations create friendships and trust. Friends expand land access through an increasingly sophisticated LANDS MANAGEMENT PROGRAM. Our institutional stewardship of public trust landscapes is currently a mess of private parcels, regulations and government incoherence. This requires organization and improvement. Only a locally developed program can re-integrate private, local, state, and federal regulations and incentives into a coherent system. Land managers can then enroll in such a program and make friends and gain benefits and freedom, within a system of responsible stewardship.

Design resources and land access organized around management empowers MORE PRIVATE OPERATORS cultivating native agroforestry systems in public trust landscapes–we start to grow food and materials while restoring biodiversity and ecological functions in our damaged and neglected commons. These emerging production systems are incubated by the network of bioregional groups, that support incubation with labor and infrastructure.

Local bioregional groups in turn independently support the development of more groups. We cultivate strength through FALL BIOREGIONAL STUDY COHORTS–offering bioregional integrated social-ecological design parallel to and complementing existing educational institutions. Through these study groups, we cultivate a NETWORK STRATEGY to increase information exchange, and how to cultivate shared knowledge on the SALISH SEA WIKI (including design resources, social and physical infrastructure prototypes, management templates, and networking strategies). We refine a shared map of a social and ecological commons; an expanding public trust landscape. We build our ability to engage in productive local governance, modify local codes to support regenerative lifestyles, and develop more field stations to gather more groups.

I am not suggesting this model as an institutional possession or an authorized effort. I am suggesting a pattern for increasing shared assets and creating new authorities, adjacent to and complementary to existing institutions and authorities. All these components would be open-sourced and designed for collective stewardship by independent but coherent groups. I am investing my imagination, labor and time in this model, because I believe it has potential. I am happy to adapt as I get feedback, I’d like to work with you.

I am encouraging our formation of prototype groups around our first field station on the Lower Skykomish on a hundred acres of riparian forest. We have three gatherings scheduled through winter. Our first hosts are the Tulalip Tribes and the Snohomish Conservation District. We have a functioning risk management model and land access agreement. Many many more sites with neglected vegetation and soils in beautiful and ecologically important locations are waiting. You, my dear reader, are part of a potential bioregional group. With friends of friends you number in the thousands. Our infrastructure is rudimentary but slowly growing: fast group shelters, portable wood fired cooking and heating, mobile composting toilets. We have much to learn and do. We have some incoming resources to help willing groups develop infrastructure. I am personally working on a simple portable high-draft wood burning heater/stove. We anticipate our first design charrette this spring of 2023. I began networking around regulatory and incentive program coordination seven years ago, and we are positioned to launch a more formal venture this spring. A flood of state and federal grant makers are hungry to fund anyone with a coherent solution to our ecological crisis. The Salish Sea Wiki is getting an upgrade and migrating to ownership by the Society for Ecological Restoration. There is work for many hands. I propose we host our first bioregional study cohort this fall.

I would love to hear your thoughts, questions or concerns. Even more, I would love to talk around the campfire at a field station.

Why Biocultural Restoration Field Stations?

A reflection on philosophical positioning on the eve of Camp Skykomish

The goal of “biocultural restoration field stations” is to create a “generative space” that is capable of exploring and interacting with social-ecological evolution in specific places. This “generative space” is useful because our culture is hurtling towards a forced transformation. Our broad global colonial-industrial social vision of endless consumption and progress is now meeting ecological limits of global carrying capacity, as we encounter the degradation of water, soil and biodiversity accelerated by climate change. I propose that study, experimentation and evolution will require what I would describe as “immersive place-based” education. 

Restoration commonly aims to increase interaction between streams and rivers and forests to undo channelization and simplification from agricultural development.

In the lowland Salish Sea, the “river forest” is a particularly poignant example of a kind of place in the thrall of complex unintended outcomes. The “river forest” is at the intersection of complex social-ecological drivers. In Salish Sea floodplains, rivers historically wrestled with forests within a post glacial geomorphic setting, to create a complex habitat mosaic–the foundation of the salmon nation. In addition to being the foundation of biodiversity and wild flood production, these same floodplain corridors contain core transportation, housing, and energy infrastructure, core food production systems, critical above and below-ground water sources, and are the flashpoint for future flood hazard under climate change. From a bioregional perspective, these river-forest corridors are exceptionally valuable and irreplaceable. Under declining global food security, urban areas will turn to floodplains for survival.

Floodplains offer a powerful experimental and learning space to engage diverse social-ecological drivers. It is this convergence of diverse forces in real places that foils our cognition. We can’t figure out how to survive, unless we learn how to live in actual places. We cannot learn those patterns until we immerse ourselves in those specific places. 

Consider the following social-ecological drivers that are at work in the Skykomish:

  • Marketplace rewards for personal achievement, both through extraction and processing of natural resources, investment in infrastructure, real estate speculation, all positioned within a global and information-based economy in flux.
  • Public infrastructure investments in common pool resources, including capital investment in fishery habitats, management of natural hazards, water quality and quantity, sometimes in conflict with enhancement of transportation and energy infrastructure.
  • The unraveling of ecological systems, including the evolution of rivers, change in climate and hydrology and forest structure interacting over geomorphic time both affecting and affected by shifting keystone populations of salmonids, beaver, ungulates and flora.
  • Cultural dynamics of belonging and separateness, with attempts to join or isolate among interdependent rural, urban, and tribal communities within the United States.
  • The structure of ownership and the control of land, from colonization to the holdings of agricultural and forestry families and conglomerates, to rapid subdivision under population growth.
  • Legal and regulatory systems and constraints, with increasing competition to control county land use zoning and ordinance systems using state and federal law.
  • Risks posed by mass migration, insider-outsider dynamics perhaps best described in Steinbeck’s the Grapes of Wrath.

Many of these drivers evolve as interest groups exercise control and power over large scale socio-economic systems far away from actual places like the Skykomish. These socio-economic systems affecting the Skykomish Valley are both divorced from place and inextricably entwined with places. In short, the local outcomes of these drivers are typically unintended. Places manifest the intersection of drivers, not the intent of individual drivers or the will of those who live in the place. This is why immersive place-based education is so vital as communities wrestle at the unintended confluence of forces beyond their control. We face predicaments without solutions, but which require responses.

The purpose of the field station is to construct a generative educational and experimental environment within a place that can explore and interact with social-ecological systems. These field stations willfully center ecological systems, as the foundation of human existence and the source of all tangible wealth. This ecological focus could be considered a bias, or as a correction to abstracted economies of the colonial-industrial enterprise. Regardless, this shift to starting from an ecological assessment of place is useful, if for no other reason than it asks us to shift perspective, while not losing sight of the essential interactions between social systems and ecological systems.

The construction of a field station is intentionally “industry-adjacent”, such that we aim to create an experimental space that lives very close to existing social-economic systems, but is also relatively independent of any one social-economic system. In the case of the Skykomish Field Station we seek a position that is adjacent to multiple sectors: ecological restoration, food and material production, and flood hazard mitigation–the farm, fish and flood nexus. This is necessary so that experiments can entrain existing resources and engage existing actors, and thus provide opportunities for substantive experimentation and feedback specific to place.

Maps and mapping become much more critical elements of place-based education.

By creating a nomadic residential capability in an industry-adjacent position we create two effects. Attending the field station involves a temporary separation from the existing social-ecological culture. This creates an opportunity to investigate the accouterments of human survival–food, water, shelter and care–in an immediate and tangible way. This experience attracts people that are willing and able to shift their position in ecological systems.  In addition, a nomadic residential experience is extremely inexpensive, reducing operating costs and increasing accessibility. This results in a system that can grow rapidly, and that incidentally supports natural disaster resilience and even explores aspects of our increasingly complicated relationship with homelessness.

At this intersection, we aim to create a novel generative space where individuals can explore the intersection of social-ecological drivers in ways that deconstruct and reintegrate the divergent forces described above. In this setting we can become direct actors, investigators, and reporters of a specific place–the Skykomish Valley–which is representative of tens of thousands of acres of uniquely important social-ecological landscape throughout the Salish Sea bioregion.

Immersive place-based education is a recognition that these divergent and conflicting social and ecological systems have and will have cumulative effects in real places. Meaningful cultivation of a resilient and regenerative culture in real places requires creative work in very entangled spaces. By observing what has happened, what is happening, and what could happen in these real places, and creating experimental spaces for exploration of alternatives, we can better understand the actual systematic environment in which our evolution will unfold.

This is particularly important under ongoing global ecological collapse.  In this way, the development of biocultural restoration fields stations is a carefully constructed open-ended response to a wicked problem.

The “undeveloped” location of the Skykomish Field Station.

Biocultural restoration field stations start with a weekend camping adventure on the banks of a river. People work, eat, sleep and play together. There we ask, “why are we here?” and seek to identify and develop small practical ways we can beneficially interact with a degraded ecological system through the practices of restoration and agroforestry. This serves as our initial topic–agroforestry and restoration in large river floodplain riparian zones and wetlands. The founders of Camp Skykomish suspect that evolution at this nexus may affect the future condition of the river forest corridor, enabling large-scale restoration and stewardship of a productive and resilient ecosystem. However the project does not end there. By establishing the field station as a viable location for groups to gather, we create the opportunity for an inclusive and inexpensive place-based education that can be replicated anywhere in the Salish Sea–the envisioned collaborative work of an “Ecosystem Guild”.

A critical place then becomes: how do we construct an educational context, that supports investigation and experimentation, and that can remain productively industry-adjacent? The educational industry, just like the restoration industry, is another social-ecological construct. In the existing educational system an immersive place-based education is only offered at a post-secondary level and only pursued by a small fraction of the population. How can the operation of a biocultural restoration field station, provide immersive place-based educational experiences that resonate within the education industry, but are also independent of that industry?

Enabling Conditions for Restoration

This is one of a series of essays inspired by a study group hosted by Joe Brewer and Diego Galli on cultivating a culture capable of regenerating the earth.  I am grateful for the opportunity to reconsider my work through this lens.

A note on the use of “restoration” and “regeneration” and “stewardship”:  I use these terms interchangeably to describe cobbling together ecosystem functions lost during colonization or more generally, civilization.  This blurry view might bother people invested in a particular philosophy.  I suggest we go somewhere and focus on the work.

Enabling Conditions for Restoration

Before I was a restoration ecologist in the Puget Sound I was a laborer. I am grateful for my shovel work because it helps me differentiate between the actual labor of restoring ecosystems, and the efforts to creating the circumstances that enable the work to occur.  Good restoration labor is enabled by the coincidence of circumstances–the right resources, knowledge and labor arrive the right place at the right time.  That enabling effort is necessary, but is not the work of restoration itself.  Right now we struggle to create enabling conditions around each new project.  This is because we are attempting restoring outside of a culture of restoration.  We not only must do the labor, but we must laboriously build the foundation upon which the laborer must stand.  Under these conditions, we spend too many resources to accomplish too little as our damaged earth continues to unravel.  However if we can lay a broad enough foundation the regeneration of the earth will be relatively simple.

What is this cultural foundation?  We will not know “regenerative culture” by the books we read, the music we listen to, or what we post on social media.  When we are ready to regenerate the earth, we will take our tools and our short lives, and we will serve plants, deepen soils, and recharge groundwater.  We will tend to the fate of each species with our hands.  We best know a culture not by its intentions, but by what it does.  While this may be obvious, it seems useful to repeat the obvious.  Our virtual lives, on this screen in front of you, or in our heads, will not restore ecosystems.  Tending the earth happens when we are hands-on and unplugged.

The Japanese have a word “gemba” which describes the place where the action happens.  Reporters report from gemba.  Japanese and American industrialists adopted the term to describe the factory floor, where the things we value are actually created. The term is now used ritually across modern manufacturing to refocus management attention to where the value is actually created–the place where laborers make things we want (see Imai 2012).  From this perspective, management is waste, and a good system works well with less management. When contemplating ecosystem restoration, and the conditions that support it, we may be served by keeping our mind on gemba.

We can have many conversations about regenerative philosophical frameworks.  But if you want to see a culture of restoration, go to gemba.  Go to the place where people meet the land and observe what they do.  Once there, you will find people struggling to do the labor of restoration.  If you ask good questions and listen carefully you can understand what they need.  You can start to imagine the tangible form of a culture of stewardship, because that culture would support the work.  In turn, if we are wise, our attention to the labor itself will shape our culture.

Design From Where We Are

In my home on the South Salish Sea, if you go to gemba , regenerative work is done by people working for Indian nations, county conservation districts, local public works departments, a handful of non-governmental organizations, and a few adventurous farmers.  This work is mostly impelled by taxes that are distributed through state and federal grants.  The grants flow into contracts to hire engineers, excavators, foresters, landscape contractors, or conservation corps.  There are a few private landowners doing the work, often at a limited scale and in relative isolation.

As a bottom-tier bureaucrat, I now sit in the middle of this system, in front of a computer leveraging legal authorities, financial accounts, paychecks, contracts and stories.  I don’t do a lick of labor.  My partners work as project managers and in turn hire construction crews to take out dams, put bridges over streams, pull rock out of rivers, dig holes and channels, fence cows, and pay landowners to pull back from streams and plant trees.  I am not saying that this is the right way or the only way to do the work, but right now, this is our community of practice—perhaps a couple thousand people in a couple hundred institutions over 13,000 square miles.

Despite the importance of restoration on a damaged earth, the nature of my industry is nearly invisible to the public eye.  Our activities only touch a few places at any time.  We do small capital projects, within in broader culture that has a limited conception of ecosystems and stewardship.  We don’t tell good stories.  When I describe my job, people politely act like they understand, but I know they don’t.

Our cash flow is a trickle siphoned off a vast industrial economy.  In Washington State over seven million people drive 61 billion miles per year.  Twenty million tons of goods flow in and out of ports, and we consume 2 quadrillion British Thermal Units of energy to generate $350 trillion in economic activity in a landscape of pavement, pipes, cables, bridges, and buildings.

By contrast, our ecosystem restoration work is less than one tenth of one percent of this industrial frenzy, and our political benefactors, reading the tea leaves of power, fund this level of work, because that is all their patrons will tolerate. After all the paperwork and planning to create enabling conditions, only a small portion of revenue gets to gemba, to change the ecosystem. This is restoration, without a culture of restoration.  If our global state credit rating falters, the restoration industry would convulse.  At this moment, however clumsy, it is still a beautiful thing, and it’s what we’ve got.  It is a situation worthy of study, and  rich with opportunity and stories.

The Case Study of Restoring Estuaries

Because we are on the emerald edge of North America we care about Pacific salmon,  a 10,000-year-old oceanic blessing on our lands and waters.  Because these fish depend on estuaries, one of our earliest efforts has been to restore the marshes and swamps at the mouths of rivers.  These are the places where young salmon transform from freshwater to saltwater creatures, and fatten up to survive the ocean. If there is too little estuary, the population is weak.  We strengthen spawning and rearing in the rivers where we live, to enable ocean survival, where we have less control.

The easiest way to restore an estuary is to reconnect the rivers to their floodplains and get all our roads and buildings and ditches out of the way.  Once unconstrained, the rivers and tides and plants do the rest.  This mostly requires enough money to hire excavators and dump trucks for a summer’s-worth of work and getting the many concerned parties to come to agreement.  In the case of the Nisqually River Estuary, this required around $22 million over 5 years to initiate restoration of around 1,000 acres–almost nothing compared to one of our road building projects.  However unlike road building, our social infrastructure doesn’t support the work.  The project teams had to create the enabling conditions.

The refuge phase of Nisqually delta restoration, the largest single estuary action to date, was positioned to captured economic stimulus funds from the collapse of the USA housing market.

In this way, over the last 15 years, the Nisqually, Skokomish, and Little Quilcene deltas have begun to regenerate, at a cost of around fifty thousand US dollars per acre.  There are still a few complexities–for example a regional superhighway still cuts across the Nisqually floodplain (as seen above) constraining the flow of water and sediment.  However, with rivers and tides free to work, these wild systems will sustain themselves forever.  There is still much work to be done.  Some smaller estuaries have been obliterated, and restoration would require excavation of vast quantities of soil, sluiced off of hillsides.  Other estuaries are laced with roads, drainage ditches, family farms, fire stations, wedding venues, airport flight paths, toxic waste and neighborhoods.  By a wicked coincidence, a significant land base for our future food security (including for 50% of the global beet seed supply)  is below sea level, in low-lying river deltas on the Salish Sea.  The ground is sinking, and the sea is rising.

So this is real work and progress.  It is also the tip of an iceberg, and if we plan it right, the point of a spear.   How do we get from a small but passionate sidecar industry that most citizens have never heard of, to a culture of stewardship and regeneration that guides our daily lives.  I would propose that we must start with what we are doing, and leverage that into something incomprehensibly larger.  I think we can best learn by studying gemba.

In 2015 I had a chance to drive around Puget Sound and ask local restoration teams what it takes to restore an estuary.  I met with around sixty project managers and coordinators in nine watersheds, ending with a report (Cereghino 2015).  I went to gemba and asked questions.  While the title was “recommendations to accelerate estuary restoration in Puget Sound”, in those meetings we were talking about something larger.  What are the enabling conditions that allow us to restore ecosystems?  Each group considered and refined the thoughts of the previous group.  They all had similar ideas about the practical barriers they faced across rural and urban project sites.  They identified six conditions.

Six Conditions

I am not saying these six conditions are the ingredients of a regenerative culture.  I suspect we have no idea of our ultimate cultural destination. It may have something to do with how we think about kinship and our responsibility to other species.  It may lead us to reconsider some of our more frantic behaviors.  Regardless, if we escape our degenerative culture, it will be through doing the work of restoration. We start where we are.

My examples describe large agency efforts I am familiar with, requiring hydraulic models and millions of dollars in construction contracts.  But at its heart we just agree to work together to move some dirt.  I bring up these large projects, not to impress or intimidate.  I believe they are at their heart no different than what a community could do with shovels (or perhaps a neighbor’s backhoe).  The enabling conditions are the same.

Around 10 years ago a local colleague described the restoration of Smith Island in the Snohomish Estuary as “faith-based restoration.”  When his team launched the effort in earnest they had no idea what it would take, and how they would get it done.  Nisqually was both a lifetime of work by the tribe and allies, and a fluke, with financing driven by panicky stimulus funding after the 2008 real estate market collapse.  The mechanisms and precedents for doing those projects didn’t exist when they were initiated.  They broke trail through doing the work.  Ultimately Smith Island required creation of a new state appropriation to support projects like Smith Island–the Puget Sound Acquisition and Restoration Fund for large capital projects.  It was the opportunity to restore Smith Island that helped create the ability to restore Smith Island.  Here are the six ingredients they needed:

Project Managers – A herd of people does not necessarily do useful work. Someone in the crowd must take the time to envision the future, and to work out the details.  They must organize the herd.  The critical skills are not ecological, but rather social.  Mobilization alone is not enough.  Although a related art, rabble-rousing is not project management.  A restoration project manager can envision the destination, and work backwards to plot the course.  Consistency matters.  Good ideas are cheap and plentiful.  Events come and go.  It may take years or even decades to deliver a complex project.  Someone needs to cultivate and nurture large project consistently, to step back and forth between vision and practice, again and again. To have this devotion, most people need some training and tangible support.  Usually this comes in the form of a paycheck from an institution and colleagues. Any institution can work, based on any cash flow.  You can push-start a project with volunteers, and then an unexpected institution might step up to play a key role.  You can create new institutions, or better yet, entrain, empower, or connect existing ones.  However, you cannot finish a project without a project manager.  It’s the existence of that individual human that counts.  It is that individual human that takes responsibility for weaving the threads.  The skill sets can be taught, but the motivation and consistency is what matters and may be hard to cultivate.  The project manager must pivot and weave with every nuance of context, not be deflected from the goal, speak carefully, and return all phone calls.

Land Tenure – Ecological regeneration must do work on land.  Under our global land ownership system just about every square inch of earth is allocated to some owner in some nation.  The complete enclosure of the globe is perhaps the great feat of the colonial age.  In my home landscape this began with vast imperial claims, allocation of huge blocks among railroads and timber barons, the subdivision for homesteaders, the attempted extermination of Indian sovereignty, the manipulation of value though construction of a spider-work of freeways and roads, and now the aggressive swapping and partitioning under a regulated real estate system designed to serve speculation and capital flow. To rebuild the river corridors of Puget Sound will require organizing thousands of land owners, one at a time.  The more finely divided the landscape the more complex this challenge.  The mechanisms for building this network are diverse.  You might buy, lease, subdivide, file an easement, or work under an agreement, a contract, or a handshake.  Land access is created through face-to-face relationships, knocking on doors, browsing county parcel maps, and noticing signs.  Land owners talk to their neighbors, and the vital ingredients are trust and motive.  In my culture, private land is guarded with a mix of pride and insecurity.  A landowner needs a chance to examine a tenant or an offer without feeling unsafe.  Governments are poorly positioned to do this work, and land trusts and tribes move quietly and carefully to acquire lands, using state and federal grants.  This acquisition system is complex and flawed, and there is no shortage of land needing stewardship.  A single Washington State grant database reveals over 2,700 acquisition projects valued at over 2.3 billion US$ over the last three decades.  What we lack are the mechanisms for cultivating ecological stewardship.  In this work our colonial institutions and allies are equipped to acquire, but ill-equipped to tend or build relationships.  Modern conservation tends to see our human communities as a destructive rabble to be kept at bay.  Institutions like to work with institutions.  That part of the problem deserves another essay.

Knowledge – Once you have people who can envision the destination and access the land, you can get to work.  You need enough understanding of the land and its creatures to know what to do.  This isn’t an abstract knowledge or just knowing the names of things.  It is not taught in a university (I know, I was there).  One ecologist mentor suggested that to understand a living thing, you must not only know the thing itself, but what is happening around it in its landscape, and within its body–its biology.  To make sense of a place, you need to step back far enough so that you can see the forces and processes and evolutionary heritage of a place.  And you must also understand each working part, and the small human strategies and tools by which we change landscapes, and how they fit into the choreography of a solar year.  This is a deeper knowledge of systems, along with the traditions of wildland tending, agriculture and construction.  These tools are unpredictable in practice, requiring the use of intuition informed by experience.  Regenerating the living skin of the earth is a craft.  It is best accomplished as a creative experiment, with unfiltered information flowing between the hand and the mind and the gut.  It also helps to have a healthy pile of high resolution topographic measurements.  Unlike cash, knowledge is a resource that builds itself over time and grows through collaboration–a positive feedback loop.  It has collective dimensions if we have the infrastructure to store, share and retrieve knowledge within a community.  You can buy knowledge into a project.  However the cloistering of knowledge in universities, professional societies, and proprietary brands, for the profit and aggrandizement of narcissistic institutions and individuals, is likely part of our problem.  Fortunately information flows easily.

Cash Flow – I think I’ve mentioned cash at least twice so far.  There are many ways to reduce project dependency on currency, but perhaps no way to completely avoid the industrial marketplace.  Industrial machines and resources produced in mines and factories born of bank capital are paid for with bank currency.  The easiest way to sustain project managers and craftspeople in their work is to give them a chunk of currency.  There are perhaps four mechanisms available to generate cash flow for restoration: public funding to provide public ecosystem services, private payments for mitigation services, sale of marketable products from restored lands, and payments for recreational or educational use of restored lands.  By far, my industry currently operates almost entirely on public funding.  To move past where we are, will require an integration of the restoration economy into our broader economy.  Until then, cash is used to buy project managers, knowledge, land access, and the reports necessary for government permission.  Without cash, everything becomes a do-it-yourself project.  Now that I have elevated the importance of cash flow, I would also like to lay it low.  We use cash to replace culture.  We have everything we need to do this work, but we don’t do it, because we have been devoured by a social system based on bank debt currency that is destroying the surface of the earth.  Cash flow solves many problems except the one that is most important to solve.  We should sit with that possibility for a while.

Local Agreement – The act of restoration or regeneration likely involves doing things differently then they were done before.  Change can create new winners and losers.  Removing rock from a river, may let the river consume a farm field. Surging beaver populations clog drainage channels and blow out culverts.  Sometimes a new system just feels wrong to the sensibilities and traditions of neighbors raised to things the way they were.  There are both subtle and direct ways that local animosity can derail a project or undermine the next effort.  Local disagreement can result in loss of access to land.  It can undermine cash flow, as funders and investors avoid controversy and risk.  Local conflict consumes the labor of the project manager, a often limited resource.  It is easier to avoid conflict then to resolve conflict once lawyers get involved.  Interestingly, it is still difficult to buy local agreement.  People have pride.  Trust is earned, and built on mutual understanding and respect.  We live in what academics call a “polycentric natural resource governance system”.  The intersections of power can be difficult to locate.  The process of building local agreement is the process of revealing hidden power structures.  Looking at this from the other side of the equation, a restoration mentor once told me, “if you are not pissing someone off you are probably not doing anything.”  So we must also learn to piss people off with respect and compassion.

Government Approval – At some point in time, if you aspire to do something at a meaningful scale, you will run into the apparatus of the bureaucratic nation state.  In the Salish Sea, I live in the City of Olympia, incorporated in Thurston County, in Washington State of the United States of America.  If I want to modify an estuary, I will need permission from no less than eight local, state and federal agencies and probably two Indian nations.  This permission is obtained through the prolonged ritual exchange of documents.  Each of these hierarchies is concerned about different things, speaks a different language, and they may contradict each other.  Their staff are overworked and are suspicious from being lied to constantly.  A complete regulatory process on a large complex project may easily take more than a year.  Not one of these institutions has the capacity to improve the system they are locked into, and there is little capacity or incentive for collaborative improvement.  An agency may face legal suits if it is either too lenient or if it is too restrictive.  You will never understand an institution by looking at their website.  To learn how an institution thinks and works you need to talk to insiders.  Show them care–its not easy in there.  Fortunately citizens can do a great deal of restoration without getting involved in this shit-show, and you might even use it to your advantage.  Governments are afraid of community discord, but are equally hungry for community solidarity.  Leaders will race to get to the front of a parade that reflects consensus and clear direction.  As with land access, government agents often lack the social networks and freedom to do the work of building community vision.  Arranging for government approval may seem like a barrier, it may also become a tremendous resource.  I would propose that in many situations the inability of governments to support regeneration is more of a symptom then a cause.  Our governments are lost in the incoherence and tumult of our colonial culture, just like we are.

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These six enabling conditions: project managers, land access, knowledge, cash flow, local agreement, government approval, are common to all scales and types of restoration.  For your home garden these conditions will be easy to sustain.  To some this list may seem excessive.  When your work becomes easy through practice, then teach your neighbor, and then learn how to do more.  As we move from parcel to catchment to watershed to ecoregion, we will need to grow into our vision.  When ecoregional regeneration is underway at home, move to the next ecoregion and lend a hand.

The purpose of outlining enabling conditions is to help us see them as a shared operating environment, and a context for design.  Small actions can cultivate the enabling conditions for larger actions, but only if we see the enabling environment as part of our shared work.  In a culture of stewardship our social infrastructure supports restoration.  Regeneration would permeate our social lives, and bind our communities.  Schools, neighborhoods, religious communities, clubs, societies, and cities would imagine themselves as custodians of watersheds in a way that shapes their relationships.

A Warning

I’d like to offer one warning.  Right now, these enabling conditions are scarce, and each institutional workgroup is tempted to act like they are alone and competing in procuring these conditions for themselves.  We are conditioned to this narcissistic thinking.  A project manager may only think of enabling conditions as a checklist necessary to generate a product for which they will be rewarded.  We still see cash flow as the solution to most of our deficits.  I’d suggest this perspective is deeply flawed, and undermines the very foundations of our work.

Look at each condition again.  These conditions are not objects to be possessed.  Each is a process that emerges from relationships.  The relationships are complex and overlapping.  These enabling conditions are in constant flow and flux.  One enabling condition can be used to nurture another.  If we are each attempting control within our narrow field of vision, we may not see the web we are weaving as a network of relationships that enable regeneration.  If we can see this, we can shape  a system that enables restoration as a natural outcome of our social processes.  If we can see these enabling conditions as a web of relationships, to which we are all contributing, and by which we are all strengthened, then we are building the culture of stewardship together.

Reconsider each condition.  What are the individual interactions that enable these conditions to occur?  What are the underlying needs that are at work?  What are the existing dynamics that feed these needs and enable these conditions to arise? How are they constricted or constrained?  Where are we wasting effort?  Your role is not defined by you, but rather by where you place yourself within a web of relationships in a landscape of possibilities.  You may need to appear a certain way at a certain time to be effective.  Your work on one project, may beneficially enable another unrelated effort.  It will serve us to slow our frantic pace, and step back, and consider our shared context.

Dave Snowden is a Welsh technologist who defined the Cynefin (ku-’ne-vin) Framework.  He would observe the conditions that enable restoration of landscapes as a “complex problem”– the challenges are not entirely knowable, and not entirely predictable.  You can’t plot a course standing on the edge of this uncharted forest.  There is no trail.  You need to proceed accordingly.  Travelling cross country in forest may be a fitting metaphor.  You may have a place you are going, but that doesn’t mean you travel in a straight line, or always have your destination in clear sight.  You make exploratory moves, and look for patterns: how the undergrowth thins under young conifers; you follow the trails of deer.  You test, observe the outcome, and learn from your experiments.  You might backtrack or you might strike out boldly.

We get to be a new kind of pioneer.  We only get to work one project at a time.  By doing the work, we become better able to shape the conditions that enable the work.  As each setback and barrier comes into view, never assume it is immutable.  Never assume you are alone.  Continuously revisit your assumptions about where we are going and the actual nature of the opportunities in front of us.  Each project, however small at its inception, offers insight into our culture, and its potential evolution.  To capture this insight requires that we become fluent in enabling conditions, and recognize them as a product of cultural infrastructure.  That reweaving of culture is our shared project, like a collective unconscious, but corporate and accessible only through doing the work of restoration itself.  You cannot learn this forest by looking in from the edge.

If you have read this far, I hope you are doomed to become a project manager.  Regenerating the earth is a hard learning path.  As you explore the complex territory of the place you inhabit, please notice enabling conditions.  Stay focused on gemba.  Consider how relationships develop.  Test, observe, and take a step.  Then test again.  Restoration advocate John D. Liu once shared with me a Chinese proverb: “you cross the river by feeling the stones with your feet.”

Notes on Creating Wild Spaces In Public Places

There is no space afforded the wild in public life.  There is no zoning for wildness.  In our cities, wild plants are scraped poisoned, and trampled, persisting in the margins.  Within the core of our settlements, no creature is valued without permit and ownership.  Individuals from desirable species are cloned and arranged for our pleasure and discarded if they get too old or damaged.

In the crannies of the parcel grid are neglected wild spaces.  This is where we dump old couches and brush.  Wild people go there to hide from armed patrols.  These wild places are too damaged to be called forest or meadow, and are repopulated with a melange of the most wild of creatures, stowaways beyond our control: ivy, bindweed, holly, rats, laurel, herb robert.

As a landscape management veteran, I was an enforcer in this order.  I was a professional supported by the beliefs, stories, rituals and taboos of my clients.  I tamed the wild.  To be a tender of the wild, we don’t get the benefit of cultural scaffolding.  We are given no clear social niche.  Restoring wild ecosystems in the midst of a manicured city is provocative and unsettling of this order.  It is as if we were suggesting that the endless effort  to subjugate all other organisms were not be necessary.

This is a slow rolling essay, where I’ll accumulating short ideas about the psychological dimensions of creating wild spaces amid human settlements: street ends, schools, parks, subdivision greenbelts, drainage ditches, road verge, abandoned lots.  Most of our neighbors do not see the wild.  We are illiterate and the wild is illegible.

If our work is to regenerate wild plant communities in settled landscapes, half our work is to help them survive the depredations of our neighbors.  This is for the hearts and minds.

With Clean Edges and Even Surfaces You Can Get Away With Anything (6/7/20)

Back in 1995 a landscape mentor told me this and it stuck.  After doing a job, we would use a blower and clean out the entrance and paths of a garden job, even if we never touched those areas.  Walking outside, the client would see everything looking freshly swept and feel good before they even looked at our work.  I remember one job I did for a client–we traded landscaping for voice lessons.  She was unhappy with her yard and wanted it more “tidy.”  I cut an edge between her shrubs and lawn, and raked all the leaves to cover the newly defined beds.  She was gleeful.

For people that don’t really see and feel plants as individuals or creatures, but rather as a textured backdrop to our self-absorbed lives, the green world is dominated by surfaces and lines.  These even surfaces and lines create order.

If you create a wild space, consider the definition of its edge, and how the orderliness of the edge creates a feeling of comfort and safety for people who might see wild plants as a challenge to order.  An edge can be a low fence, a set of bollards, a mowing curb.  An edge can serve a double function as a hydrologic feature.  But cut it clear and hard.  Use a french curve for inspiration.  Mark it as claimed by some human force.  For some it will signal that the wildness is contained and therefore unthreatening.  For others it might signal that someone somehow owns the wildness and therefore they should not interfere.  Use the beliefs and rituals of ownership to claim the space.

The same applies to entering the wild space.  We do not tromp through another persons garden, but we fee entitled to trample any wild space as if it were our own.  Give special attention to trails.  Boldly mark entrances.  Follow and bend natural flows.  Use brush piles and aggressive plants to steer and shape visits by outsiders.  These paths also allow for tending, and like all garden paths, becomes a choreography for relationship.

In this school wild garden, small logs were used as bollards, and a small woven fence reinforces a natural entrance.  A strip of lawn is maintained between the sidewalk and the edge of the wild to allow paved traffic to spill over without violating the implied barrier.

Ecological Site Assessment

This page is reserved for tactics, resources, and results of site assessments methods we are testing in the Green Cove Watershed.   Site assessment is usually at the scale of a parcel or cluster of parcels (read about systems assessment for stewardship design).  It is a form of study in preparation for restoration or protection (read about three capabilities).  I prefer to assess in bloom, drying or harvest because of fair weather, full development of leaves and flowers, and the overlap with site preparation (read about the eight seasons in general, or more specifically about cycles of plant-soil work.)

Climate varies predictable nuance across the lowland Salish Sea, and so is more a matter of general education than site specific analysis.

Landform, Soils and Water

Initial assessment of topography, soils, and hydrologic patterns in the Salish Sea benefit from the use of state and local data, with a geographic information system.  The Guild can publish watershed scale analyses as KMZ files, which can be viewed using Google Earth Pro.  We can develop common data sources and methods for the technical work, and also teach strategies for viewing and interpreting local data, on the desktop and on the ground.

  • Google Earth Package For Green Cove Watershed – includes DNR streams, waterbodies and soils, LiDAR derived flow pathways and depressions,  County wetland and parcels boundaries, Urban Growth Area boundaries,  and Ecology wetland probability.  We need to further standardize contents and cartography… ideas welcome.

Vegetation Inventory

A starting place for a site assessment is a vegetation inventory–a list of all the plant species present within an area.  The overall assemblage and species distribution can tell stories of the site history and condition.  We are developing a standard set of tools and protocols for visiting a site, creating and interpreting a professional quality plant list, and sharing that documentation with other guild members.

  • Lowland Puget Sound Plant List – a working product that includes 445 of the most common lowland plant species you can sort by form, family, or wetland code.  We are adding additional non-native species over time, following USDA conventions.  This is a “lookup” reference for all subsequent products using 6 letter codes
  • Vegetation Inventory Sheet – A form I can pull up on my phone using a Google Sheet app, when exploring a new vegetation patch.  It lets me produce a professional quality record in a few minutes using six letter codes (PSEMEN = Pseudotsuga menzeisii).
  • Forest Observation Skill Sheet – our first skill sheet–a condensation of forest ecology topics, to support a “newbie” in making observations of a forest’s structure.  We can complete additional skill sheets and other self-study aids.

Vegetation Inventory Atlas

The embedded google map below is a prototype of our data management strategy.  Each polygon links to a stable “place page” on the Salish Sea Restoration wiki.  From there you can get a site introduction and  follow links to relevant documents, including vegetation inventory sheets hosted on the guild’s google drive.  The overall structure is both free, and fairly resilient under update.  The wiki page and google map remain stable, while the KMZ file and information stored on the wiki page fluctuate.   Thus you can add a new site, or add additional information about sites, without updating the underlying architecture.

Workflow

Below is a proposed standard new site visit protocol that establishes a spatial location and an associated wiki page.   This is roughly similar to the larger scale pattern on the watersheds page.

  1. Research soils, hydrology and canopy from desktop and anticipate vegetation zones.
  2. Arrive at field with data and smart phone (or synced sheet) and paper aerial photo with draft zones.
  3. Use Google Docs App to copy new vegetation inventory sheet to public folder and name appropriately.
  4. Use Google Sheet App to complete vegetation inventory, sketch survey area boundary.
  5. Add any new species to the master plant list, clean up the sheet, and add any notes.  Copy a view-only link to the sheet.
  6. Return to desktop, use Google Earth Pro to create and name a new polygon and add to vegetation survey folder.
  7. Create a new sub-section in the wiki-page for your place.  Add the view-only link to your vegetation inventory sheet.
  8. Save the wiki page, and copy the wiki page address to your Google Earth polygon.
  9. Save all polygons in your Google Earth Folder (including new survey site) as KMZ (add date to file name).
  10. Open Google Map, and upload the new KMZ into the existing map, and delete the old map (this should update all web based maps.)

Three Capabilities for Stewardship

Green Cove Watershed could be the most cherished stream in South Puget Sound.  Olympia offers art shows to promote “the importance of salmon to our community.”  The Evergreen State College cultivates “creative, critical thinkers … for environmental work and leadership.”  However, if I want to understand stewardship, I listen to the swampy stream that sits between them.

Image: Wild Fish Conservancy (Glasgow 2018)

Most people I meet don’t know Green Cove Creek.  We don’t see Mud Bay Road as an indistinct saddle marking the Southern divide.  We don’t notice how our road causeways have walled its headwater swamps into cells, or where our polluted discharge trickles in through glacial swales.  We guess at how many different kinds of salamander have survived.  They wait for warm night rains to crawl our roads.  We don’t count the Green Cove chum thwarted at Country Club Road culvert to never make their nests.  We don’t gather or forage.  When we need water, we extract from injected well casing.  When we need food we bring it in on trucks.  We don’t see the land in front of us, and so how can we understand where we are going?

This discordant gap between the social narratives in our heads, and our relationship to the land in front of us, may be the cornerstone of our ecological crisis.  Each day we express in miniature, our relationship with the Salish Sea.  The most brutal parts of our colonial project are mostly complete, and unremembered.  Our new homeland has been tamed, made quiet, marked with deep wounds, drying out slowly with road ditches.

Green Cove Watershed is marked in purple, with surface water flow in blue, regulated wetlands are in Green. Grass Lakes collects runoff from West Olympia (1), which then flows into the Kaiser wetlands to the most frequently used amphibian crossing at Kaiser Road (2) amid forests protected by Capitol Land Trust, before going under Evergreen Parkway and into the Green Cove ravine. In 2018, over 500 chum returned to the creek, struggling to get upstream of two culverts (3). The proposed Green Cove Park subdivision provides an example of poor stewardship (4), while students and teachers at Hansen and Marshall schools (5) are positioned in the middle of the watershed, and want to study where they live.

There is a quiet struggle at Green Cove Creek.  Twenty years ago the City was impelled to buy the Grass Lakes, and signed the Green Cove Watershed Plan–another treaty.  South Puget Sound Salmon Enhancement Group is just starting to explore the salmon-bearing habitats, a project recommended 20 years ago.  Project managers grimace at the fish-barrier culvert buried deep under road fill (have we ever abandoned a road, for the love of a stream?)  There is a volunteer that counts salmon redds.  The Squaxin Nation struggles at more urgent sites.  Between Streamteam, Stormwater and Parks, the City affords a little work here and there.  A couple middle school teachers sustain a science and service program, and Native Plant Salvage Foundation lends a hand.  Capitol Land Trust stopped buying land in Green Cove when Thurston County started hoarding all our Conservation Futures money to offset prairie development.  Sometimes groups of college students wander by and look.  Government biologists count mud minnows.  Community activism ebbs and flows with each new subdivision proposal.  Does this add up to stewardship?

A stig is a old English hall or home; a weard is the ward or guardian.  Steward is a verb.  If we don’t guard the hall of Green Cove Creek, what do we expect for the Salish Sea?  The number of institutions dabbling in Green Cove offers an illusion of stewardship.  I propose that we fundamentally lack the social infrastructure to be stewards our watershed.  Don’t take this personally; it could be said for any watershed.  Anyone in the ecosystem industry can tell stories.  Watershed stewardship depends on three practical capabilities that emerge from culture.

STUDY – First, we must be capable of study.  I don’t mean sporadic environmental education lectures, but rather that we have the mechanisms by which every citizen can grow to deeply understand their home. This means that we gather and organize evidence and knowledge, and share it with each other constantly.  We remember together, and we observe the land and synthesize shared knowledge of where we live.  This capability cannot be found in our schools nor our governments.  We must become again, our own carriers of knowledge, and we lack the rituals to do the work.

PROTECT – Second, we must be capable of protecting.  All our laws, acts, plans, and restoration projects will not defend the watershed.  At this moment in the watershed, a Puyallup developer wants to build a monocrop of 181 single family homes on an illegal garbage dump located a five-minute drive from 11 toxic waste sites.  We struggle to push our city government to negotiate on our behalf.  This is just one of a monotonous series of development proposals grinding away at the last forests and soils of Green Cove Creek; each trying to extract the maximum, and give the least.  Do we just wait for the next one to roll in?  Protection is more than effective resistance (and our resistance could be much more effective.)  We must enforce good planning at the permit counter.  We must enforce clear vision at the ballot box.  We need the tools for regenerative development, so we don’t depend on out-of-town profiteers to tell us how to build our home.  Mass migration and climate change are coming.  Do we understand what we need to do?

RESTORE – Finally we must be capable of restoring.   We can be allies to beaver clans, infiltrate water, capture carbon in forests and soils, and re-weave the web of life.  We need not wait in line for state and federal grants.  Restoration can be a community celebration that only requires of us that we understand and take control of our existing shared resources.  Restoration is an educational opportunity for our schools.  Restoration is employment that builds knowledge, belonging, and wealth.  We can restore a watershed with a graduate student, a farmer’s backhoe, and a middle school nursery.  What exactly are we waiting for?

In practice, our capabilities to study, protect and restore are interdependent, and will work in synergy.  These capabilities will not be given to us.  This is a do-it-yourself retrofit that we must earn.  We must rebuild the “common hall”.  This requires continuous practical effort.  I am doubtful that we should build new institutions.  We have plenty of institutions.  What we need is to lean in and shape the ones we have, to become part of a clearer vision and a stronger effort, more deeply rooted in a culture of stewardship.  This requires that we shape how we spend our lives, and nimbly gather in shared work.  I hear my professional colleagues say we need more resources to be stewards.  I have to laugh. We squander more resources than anywhere on earth!  You don’t buy a culture. Everything we need is right here.

End Note – Green Cove Watershed are lands of the Squaxin Indian Tribe ceded under duress, cared for by their ancestors since time before memory (probably at least 400 generations).  Our stewardship is described through ALL our relationships.  We are in a relationship with the Palouse hills, the floodplains of the Mississippi, the Amazon Basin and the coastal peatlands of Borneo.  We give away our agency, and then our agents work in our name. There are stewards also struggling in those watersheds, and they also need our help.

Three Simple Goals: Water, Biomass, Diversity

Civilizations degrade ecological systems.  Ours is no different (see the essay on restoration for a summary.) Empowered by fossil fuels our destructive power outpaces any potential for natural recovery.  We are the global keystone species, and it isn’t pretty.  Our current condition is, ironically, both revealed and obscured by professional science and management.

On one hand professional science is able to imagine, detect and summarize our profound modification of the surface of the earth, from our doubling of nitrogen fixation, to shifting atmospheric composition, to declining global primary productivity and biodiversity.  We are surrounded by systematic detailed peer-reviewed evidence.

The language and analysis of scientific ecosystem management, on the other hand, is so arcane and inaccessible that most of our neighbors don’t know the playbook, and may not even realize they are on the team.  Government information workers decipher ecosystems, and weigh social and economic significance, largely in private.  We do a poor job building a shared base of knowledge.

In back rooms, lawyers leverage every uncertainty in hand-to-hand combat over risk and liability.  Legalism wrestles over words and numbers.  What width of forest buffer, on average over a whole landscape, lets us avoid liability for killing fish?  How many cases of cancer caused by polychlorinated biphenyl ingestion can be glossed over during the next election?

Questions like these reflect the underlying pathology of our stewardship, more then reflecting the interests of people in communities.  At the highest levels of leadership, we ask ourselves, “exactly how little do we have to do” or “what little more will satisfy popular demand”?  A local leader doesn’t yet need a coherent ecological platform to gain and hold power.  In modern environmental management, communities are not participants in a web of life, they are “interested stakeholders.”

The truth is that we have lots of restoration projects, but very few restored watersheds.  Projects are occasional, while deforestation and pollution are constant and grinding. If we don’t effectively restore any one thing in particular, what are the chances of restoring the whole Salish Sea? Is ecosystem stewardship just another politicized industry and legislative product, competing in the marketplace of ideas?  Do we chase after symptoms while ignoring the disease?

We need some simple ways to talk about ecosystems that help us think clearly. Understanding ecosystems doesn’t have to be complicated.  The best tool does good work with the least fuss.  I’d propose that three measures, tell us most of what we need to know about our stewardship of a watershed.

1. Water

What do we do with the rain?  We can either capture and store it in wetlands, vegetation or groundwater, or we can send it as a polluted flood to the sea.  Water is the first fertilizer, and our droughts are lengthening, and will bring more fire.  We can directly observe our waste of water by walking the watershed in the rain.  We could capture and store the rain and recover the functions of our cut forests with common tools, if it weren’t for property rights and aquatic ecosystem regulation.  Learning how to protect and store the water together is our first great challenge. (Read more)

 2. Biomass

The surface of the earth is cloaked and transformed by plants and their remains.  Plants create soil, and I could have just said “soil” instead of biomass, but I’d be missing the forest.  Our rainforest home is among the great woody carbon reserves of the earth, accumulating hundreds of tons per acre of mammoth tree boles and layered coarse woody debris.  This biosphere is our home, and we are just little crawly things on its surface.  Before we learned how to burn fossil fuels, we were already busy cutting forests, overgrazing hill-slopes, and turning soil to dust and pavement, mostly to grow food, house people, or feed smelters.  Biomass mediates the water cycle and forms the structure in which diversity resides.  Rebuilding biomass, while feeding ourselves is our second great challenge.

3. Diversity

When we restore water and biomass over a large surface of the earth, we create the conditions for life.  The biota around us are a legacy from a once abundant world, that we either cherish or squander.  Global ecological integrity is disintegrating from agricultural development, elimination of predators, over harvest of keystone species, chemical disruption, habitat destruction, and our assisted migration of diseases and pests.  But evolution still works.   As we destroy species, we diminish creation.  As species form new communities, in search of new equilibria, in a new and changing climate, we are likely to experience a millennia of instability.  Whether we like it or not we are no longer in control (if we ever truly were) but we do profoundly influence the processes.  Stewardship of diversity will be challenging and painful, but we can look deeply at the populations that remain, and play our humble role, largely of self-restraint.  Using our influence to wisely protect our evolutionary heritage is our third great challenge.

With these three goals in mind, all of us can work on our watersheds.  Complexity doesn’t help.  Right where we live, we are either catching more rain, or less.  Our biomass reserves are increasing, or decreasing.  Keystone populations are expanding, or crashing.  We can map our strengths and weaknesses watershed by watershed and get to work.  We can see change for better or worse, outside our door, and down the street.  This doesn’t require scientists–it requires personal commitment. This is a simple thing.  By retaining water, building biomass and protecting and restoring biodiversity, at a landscape scale we can build a strong foundation for the future, whatever it brings.  If we fail at these three simple tasks, than we deserve the ruin that we will have earned.


A special thanks to John Liu and his vision for the simple goals of Ecosystem Restoration Camps.

Post Script – When I say “our” watersheds, I am using the possessive  primarily in the sense of our responsibility.  The challenge before all others is to take responsibility for our own behaviors.  Without a measure of self-discipline, all will be lost.  When I ask us to consider “our watersheds” I mean ALL the watersheds from which we extract or derive our sustenance.  If you buy beef from Brazil, then the Amazon is your watershed too.  Once you put your hand on the balance, it cannot be undone.  Its the same in our forested foothills, as  disposable chopsticks, disposable packaging, and disposable housing feeds the aggressive and endless clearcut in our foothill forests, reducing them to fiber factories.  We cannot tend our watersheds at the expense of another, and pretend any moral foundation, nor can we adequately steward our lands where we have relinquished our sovereignty.

The Cycles of Plant-Soil Work

Plant-soil work is perhaps the fundamental process of ecosystem stewardship.  Every landscape on earth is shrouded in a green cloak of vegetation, with a particular structure and composition.  Plants created the earth as we know it.  The line between plants and soils is difficult to draw.  Plants are a manifestation of a living soil ecology, and the soil ecology is aggressively modified by plants.  We almost always work on both together. This land cover drives hydrology and carbon storage, and is the infrastructure of biodiversity.  

Like most human endeavors, our work with plants and soils follows the annual cycle of the sun.  The Eight Season Year is  a framework for organizing that annual cycle.  Plant-soil work occurs everywhere locally; a primal intersection of social and ecological systems.  Some kind of multi-scale systems assessment is useful for clarifying the context of plant-soil stewardship.  Our work has layers of purpose and meaning.

Plant-soil work is infinitely varied, but follows recurring patterns.  Buried in tradition there is some goal of achieving a desired future state.  If you are farming for a living, that desired future state is an easy to harvest field full of product you can sell.  If you are cultivating an ecosystem, your desired future state may be an evolutionary trajectory that plays out over 1,000 years.  The important part is that you know where you want to go.  Without clarity about where you want to go, you cannot pick a target, assess a complex social-ecological system, or design a good soil-plant treatment to get you there.

Most soil-plant treatments are built of three parts:  1) disturbance, 2) propagation, and 3) aftercare.  This is a simplification, as a “treatment” may include several cycles or repeat steps, but we can always find three parts:

  1. Disturbance – Vegetation fills every viable niche on the surface of the earth.  To introduce a new vegetation pattern we apply some destructive force, to create a vacancy.  Nature does this with floods, landslides, fire, and herd animals.  Humans use tillage, mulch, animals or poison.  As part of our disturbance we may modify soils, changing their structure and composition. Because disturbance takes work, we constantly ask, how little disturbance is necessary to create enough of a vacancy to achieve the desired state?
  2. Propagation – The second step is to introduce some propagule into our vacancy.  A propagule can be seed, a cutting of stem or root, a bare root plant, or potted stock.  Perhaps we are only activating seeds sown in the seed bank by previous generations.  The production and transport of propagules takes work, and less developed plants are better able to adapt to a new niche, but less able to withstand stress.  So we constantly ask, what is the smallest propagule that can establish on a site, and initiate the transition to our desired state?
  3. Aftercare – Once our intervention is complete, the wildness of the earth re-asserts itself over the site.  Propagules are subject to competition and stress.  We mediate that process, by supplying nutrients or water, or with selective disturbance.  Aftercare is always more expensive than the initial disturbance, because we have to work around our propagules.  We now pay for any poor choices in steps one or two.  There are many risks:  poor site assessment, ill-informed species selection, too little disturbance, too small a propagule, a labor intensive layout, a bad season, poor quality stock, or unskilled planting.  We pay for any weakness in design with aftercare.  If our design is poor, or we are unlucky, we can fall into spiraling aftercare costs, or fail to achieve our desired change.

Every plant-soil treatment successful or not, emerges from a vision of a desired future state.  In restoration, we push ecosystems from one wild state to another wild state.  Given the complexity of wild things, lack of clarity in design is not surprising.  What exactly is the desired change?  Where are we going and why?  It is easy to be lazy in our intentions and purposes, and play it by ear.  I suspect that if we are going to restore hydrology, carbon stores and biodiversity at the scale of watersheds, our soil-plant work must become a disciplined art.  This art is built from a deep knowledge of place, species, tools, technique, and the annual patterns of vegetation.

Evolved vegetation is not entirely random.  What we see in a plant community are the results of forces at work in a place.  Those forces precede us and remain after we leave.  Vegetation ecologists attempt to explain the factors that control vegetation, and their theories can help us organize our thinking about soil-plant work, so we are working in alignment with ecological drivers.  In particular we pay attention to the role of disturbance and stress.  These drivers change as a stand recovers from disturbance (a pattern called “succession”), and different species have traits that are adaptive to circumstance.  However the evolution of a patch of vegetation is also affected by more random processes of assembly, like who’s there now, and who shows up next.  The narrative of vegetation is like an story where the details change, even as the themes remain the same.

Lets take each of these concepts in turn:

Disturbance

Each site has a regime of disturbance.  Disturbance involves physical damage to a plant.  Storms rip at stems and leaves with some combination of wind, ice, snow, and cold.  The flooding of rivers and streams can scour or bury, and saturated slopes slump and slide.  Grazing herds nip and trample more noticably than the quiet predation of insects or fungi.  Living under a big-leaf maple insures an annual burial under smothering leaves.  Plants have a traits that make them more or less resilient under disturbance, such as winter retreat to roots, stems that form roots, or the production of toxins.  The frequency, predictability, intensity, and homogeneity of disturbance determines who lives or dies on a site, and shapes structure and composition.

Stress

Optimal growth is achieved in warm, moist, and oxygenated environment in the presence of nutrients.  In the absence of stress and disturbance, life in a patch of vegetation becomes a race for light amid rampant growth.  As growing conditions become less than ideal, this causes stress, a reduction and eventually cessation of growth.  Cold, heat, prolonged inundation, nutrient deficiency, or drought can slow growth or force dormancy.  Each species has traits that make them more or less resilient to different stresses: waxy leaves, deep roots, or symbiotic relationships with bacteria or fungi.  As with disturbance, stress comes in different frequencies, intensities, and with variable predictability over an annual cycle.  Species that are resilient to the stresses of a site will come to dominate the vegetation.

Succession

Following a severe disturbance, there may be more resources available to an entrepreneurial propagule.  As vacancies are filled, and the annual regime of stress and disturbance settles in, the rewards for exuberance decrease.  Even as the work of plants increasingly moderates climate, retains moisture, and cycles nutrients, those resources are shared among increasingly entwined co-habitants.  The species that are successful after disturbance shift over time, from fast growers, to those that are able to thrive under the stresses of cohabitation.   This process is called succession, and as plant-soil workers, we can anticipate, accelerate, arrest, or reset successional processes to suit our purposes.

Assembly

While we can talk about pattern, the reality of vegetation is formed by uncountable individual experiences by individual plants.  Any pattern we might detect emerges as a general direction, driven by a mix of potentially erratic processes.  While succession is a tidy and useful story, the development of vegetation does not follow a predictable path.  The sequence of arrival, specific interactions, and random events may create unexpected changes in the story-line of vegetation.  Under climate change, past performance may not indicate future behavior.  As short lived species, we humans may have a very limited understanding of long-lived cycles and patterns.  We may find patterns out of habit, to soothe our confused minds, while the wild is sublime in its chaos.  It may be more useful to see evolving vegetation as subject to a variety of filters that winnows down the pool of potential species, to those that can complete the challenge of life in the moment.  A variety of young ideas, under the umbrella of assembly theory, attempts to makes sense of emerging unpredictable reality.

Annual Cycle of Work

Armed with this language, lets walk through the Eight Season Year beginning in Springtime (early spring).  Bud-swell (late winter) is a culminating flurry of activity, when woody plant propagules are inserted into a site during cold weather dormancy.  In Springtime we catch our breath, and look at what we have done.  We anticipate our our past mistakes, and begin aftercare and disturbances in preparation for the next planting.

Springtime (Equinox)

By the equinox, all our woody planting should be complete, and we can turn our attention to aftercare of old plantings, and disturbances to prepare for new plantings.  We can observe leaf and shoot development rate and color, and get a feel for which plantings are robust, and which are weak.  While the ultimate outcome is yet to be seen, and first year growth varies among species, we begin to feel which of last years treatments are effective.  We get to see the regrowth in last years disturbances, and the level of competition.  Any detail weeding should be done in spring time, before weeds are rampant.  Tillage windows become abundant, although spring seed beds will be rougher than those begun in fall, and seeds are sown when not requiring cold stratification.

Bloom (Mayday)

Bloom is the peak of above ground growth, and the moment when new plantings are over-topped.  Vegetation is succulent, nutrient rich, and easy to cut.  This is the opportunity to chop and drop, or cut and carry material to smother planting sites for next years growth, and to protect new plantings from drought.  The mechanisms for providing water as aftercare should be in place, as drought can come in bloom, and water may be most effective if applied in occasional deep irrigation before drought stress arrests growth, so that new plantings can sustain root growth into the drought.  In bloom, the flowering details of species are easily observed, but spring ephemerals are still present.

Drying (solstice)

Earthwork and tillage is easier while there is still some moisture in the soil.  After the rush of cutting and piling and before the heat of summer is the ideal time for all outdoor construction and earthwork.  Building trails and bridges.  Cut and carry can continue in moist areas with rampant growth.  The seed formation and collection season has begun.

Harvest (Harvest)

By Harvest, the natural dry-down may create intense stress.  In new plantings, some of this stress is beneficial, driving plants to commit to deeper roots.  Seed harvest is in full swing.

Leaf Fall (Equinox)

With the return of rain, the aftercare season is over, but planting season has not yet begun in earnest.  This is a good time for starting a new round of layering.

Frost

Frost is the beginning of the dormant season, and the ground is less likely to be frozen than during darkness.  Out-plantings, particularly evegreens, will have the maximum time to adjust to their new settings.

Leaves are abundant, and can be collected, moved, stockpiled or concentrated to achieve disturbance effects.  Some municipalities will stockpile or even deliver leaves.  Tree services begin their winter storm cleanup work, and will be motivated to dump ramial chips.

Darkness

After a flurry of planting in frost, and after the holidays, attention turns to cuttings, which benefit less from the early out-planting.  Clear days bring frozen ground, and inefficient planting.  Bare root orders arrive, having been dug by nurseries during Frost.  Planting in Darkness makes you wonder why you didn’t get your work done during Frost.

Budswell

As day length expands, buds begin to break, stimulating root growth.  Elderberry and osoberry pop first, and any bare root plant or potted stock must go in the ground or be replanted into nursery beds for another summer of watering.  Weedy root-mass not sufficiently damaged by disturbance will start to push through rapidly decomposing mulch.  Leaves and cuttings from last season are almost gone, while wood chips persist.  This is the flurry, before you take another breath, and switch to aftercare and a new wave of disturbances.


Each plant-soil treatment is an experiment, based on a prediction (sometimes unstated or unclear).  To the degree each treatment is well-designed, and we watch our results, we can advance a shared art.

Our greatest challenge is to find and let go of useless work.  Can we use the right tool, and the right technique, at the right time, and create the desired result with less effort?  Can we create a sequence and structure and timing of disturbance that also reduces the labor of aftercare?  Can we use accelerated assembly and succession to let time do our work for us?  This is the mystery ahead.

Right now, I suspect our plant-soil work is rudimentary.  We are good at trees, because they are easy.  Biodiversity is harder.  Succession is haphazard.  The dynamics of assembly, mysterious.  We use lots of oil and buy lots of stuff.  Labor is separate from design, and monitoring is generally absent.  Staff turnover is rapid, and plant-soil workers are the last to be consulted and the least paid.  We don’t respect the art.

Further, most of us don’t use wild plants, and so we barely care about the wild communities we tend.  A young forest with fifty species might provide twenty products to enrich a community, and harvest might be just another tool to guide assembly.  But we are divorced before the planting is even done.  The designers have gone home, and the crews toil in the rain, and may never see the site again. No wonder we remain ignorant.

The cycle of the year suggests a web of practical skills from ecology, horticulture, ethnobotany, pedology, phenology, silviculture, agriculture, botany, allometry, biology, agroforestry, and culinary arts.  You can follow the roots of these sciences deep into time before memory.  Each thread of this web ties us to the land.  Each place is a new story unfolding.

Systems Assessment For Stewardship Design

DRAFT

This is a framework for integrated social-ecological systems assessment to support the mission of the Ecosystem Guild.  WARNING–very abstract stuff.

Stewardship is a two step dance.  You observe and then you act.  Then you do it over again[1]Different authors differ in their choreography of the dance, from Hollings’ early descriptions of adaptive management, evolved into the Open Standards for the Practice of … Continue reading.  All of our knowledge, skills and technologies just facilitate this two step dance.  We are trapped in the current moment, we learn by comparing present to past, and we speculate about the future.  Stewardship of ecosystems is the ultimate strategy game[2]A portion of my fascination with this work, and my approach, comes from playing the classical East Asian strategy game of Go.  Many complex games offer metaphorical guidance.  We are all players.

When I play a game, I like to have a strategy to organize my work.  If we hope to play such a game as a community, a shared model is necessary to support our collaboration[3]Many strategic approaches depend on construction of shared models, such as Stroh’s Systems Thinking for Social Change, group exercises in Value Creation Chain evaluation proposed under Lean … Continue reading.  In this infographic I offer my 30-year synthesis of how to assess the game board of ecosystem stewardship (also available in PDF format).  It has been a vexing journey, and a learning experience, with ideas gathered from many different sources, so it seemed like a good idea to pause for a moment and try to scribble down a map.  The next 7,000 words are just an expansion of this graphic.  This is a draft and I have a lot to learn.  Assessment of the design environment is so central to ecological work.  I will likely be revising this the rest of my life.  There are footnotes where I try to credit my inspirations.  Thank you.

Before diving into the essay, here is the one paragraph version full of lingo:

“Stewardship is achieved through the design of behavior at the interface of social and ecological systems. Systems are nested and operate at multiple scales–the earth is a shared system now dominated by human behavior.  While ecological systems are tangible, social systems are largely a fabrication of consciousness.  Stewardship design requires identifying a system of appropriate scale for our work, and discerning both ecological and social context, at both larger and smaller scales than our system of interest.  Large scale structures and processes are often stable and slow, and smaller scales are often fast and evolving.  We are both influenced and inherit our purposes from our place within larger scale systems.  We act on these larger systems only through the cumulative effects of work within our zone of influence.  There are likely optimal scales at which to cause a durable change in system state. The complexities of systems are best integrated in places at a human scale through design.  Design is driven by values.  At any scale, the functions of a system are shaped by the interactions among processes and structures, resulting in the emergence of functions or dynamics.  Often a few defining processes regulate system dynamics.  Some system dynamics are stable and generative, and we describe these as natural, human, or economic capital.  Many different forms of capital are realized and sustained at different scales.  Stewardship is the process of developing and sustaining diverse forms of capital through the cultivation of effective individual actors within a nested human-ecological system.”

Ecological Systems, Human Social Systems, and Design

Ecological systems and human social systems interact, but are fundamentally different.  Ecological systems are made of tangible features that can be measured.  If we spend the time, we can sense the flows, fluxes, and transformation of energy, water, nutrients, and gases[4]This nomenclature for ecological processes is inspired by  processes-based models developed Simenstad and others, and will be revisited later, however the division of systems into four elements … Continue reading.  Human social systems by contrast, are mostly inside our heads.

Between ecological systems and humans systems there is overlap, where the ideas in our heads lead us to work on the land, and some of that work can change ecosystem state[5]“Ecosystem state” is common short hand for the structure of a system at a moment in time.  In turn, our observations of ecosystems can inform the ideas in our heads about social systems.  How we obtain resources and interpret scarcity is an example of this interaction.  Our relationship with nature is a story in our head, that is played out on the ground.  This”place and moment of social-ecological overlap” is important, because as ecological systems and human social systems collide it determines the fate of civilizations.  Stewardship is focused on shaping this interaction so that it aligns with our values and sustains the well-being of our descendants.

My assessment of social systems is focused on humans.  There are beaver social systems and wolf social systems that we barely understand.  Humans, however, are the earth’s dominant ecosystem engineer.  Our efforts eclipse the work of all other beings.  We do not tolerate any creature that contests our domain.  The global well-being of most species is now along for the ride as we careen along a precipitous road mountain, dependent on our ability to drive–our emerging capability of collective design[6]I suspect that collective design capability is different than individual design capabilities and that individual design capabilities may not be sufficient to solve ecological stewardship problems..

The global well-being of all species is now careening along a precipitous road mountain, dependent on our ability to drive–our capability for collective design (Image from Pakistan Today by Javed Azam)

For the purposes of stewardship our social system and the ecosystem are not separate.  They are one integrated system.  I often avoid the word “natural”.  Both human-built environments and “wild” places are part of a single inseparable social-ecological system[7]The term “social-ecological system” has emerged in part form the adaptive management community described earlier, the subject of increasing scholarly work.  Our built environments are just those patches of earth that we have most aggressively engineered.  While we may wholly transform a watershed it is still an ecological systems.  Our idea of being somehow outside nature is only a story of rapidly declining utility[8]This is not intended to suggest that when humans detach from evolutionary processes and systems that there are not consequences in our mental landscape.  We could likely describe a wildness gradient … Continue reading

I am using the word “design” both broadly as a widely applicable process, and precisely, as a specific phenomena.  We carry all kinds of stories and understandings in in the clutter of our heads.  Not all of these affect our designs.  Design is the mechanism by which we take the stories in our heads, and turn them into tangible work in ecological systems. Our designs may be simple or sophisticated, and stack one upon another.  However, we still work one design after another, one work after another[9]It is important to differentiate between work and talk.  It is the work that affects ecosystems, and the talk only counts when it changes the work.  Sometimes our designs are so ingrained, and our work so ritualized that they are almost subconscious, like when we repeat our design for how we get to work in the morning, burning fuel and spreading copper dust and oil residue, racing along perpetually maintained travel paths, built of compacted rock and tar.  We carry all kinds of values in our heads, but the ones that count are the ones that get into our designs and our work.  The form of the dance depends on not only our values, but our ability to integrate our values into our design process.  In this way I talk about design broadly as a process that everyone uses all the time for just about everything, but it is specifically how we translate internal or shared values into external work.[10]There is a feedback loop here, recently clarified by a colleague Joe Brewer, who introduced the concept of “social niche formation” whereby we create inherited infrastructures that guide … Continue reading

A mixture of road toxins is causing broad scale mortality of coho salmon as they enter streams and before they spawn across Western Washington–an unintended consequence of our entire transportation system, which is now driving the construction of yet more infrastructure that we will need to maintain forever.  (image from Puget Soundkeepers)

Design is the only mechanism by which we exert control over our behaviors.  Our effectiveness as ecosystem engineers depends on our design skills.  How our designs perform, depends on both intentions and how our designs are fitted to the design context.  We can have good intentions, and bad designs and fail to express our values.  Our ability to create an effective design depends on our ability to assess the design environment.  If we get the assessment step of the stewardship dance wrong, the action step is more likely to be misguided and misshapen.  This seems simple, except for the complexity of our design environment.  We are working in both ecosystems and social systems, and both systems are operating at multiple scales simultaneously.

Scale As Both Purpose and Mechanism

Little Wheel spin and spin, big wheel turn around and around…” – Buffy St. Marie (YouTube music video)

In my diagram, large scale systems are on top, and smaller scale systems are below.  I could have just as well have drawn smaller scale systems floating in an ocean of larger scale systems.  Small actions exist within a larger context.  When you dig a swale, you are working within a soil series and in a hydrologic cycle.  To understand larger scale systems we think about larger areas, and longer periods of time.  Most of our lives are lived at smaller scales, over short time cycles, adapting to circumstance.

Figure 2 – the social-ecological system model with the role of scale in design, relative to our zone of influence as stewards.

The large, long cycle systems in which we live influence the context for our work, both ecologically and culturally.  Large global patterns of temperature and precipitation determines what lives or dies, from a tropical rainforest to an arctic desert.  Among human systems, large, slow cultural stories about agency and ownership drive the structure of households and workgroups, from hunter-gatherer enclaves to the authoritarian networks at the heart of global empires[11]While this is a flip generalization, it is also intended to point at a particular aspect of context.  Our social systems existing within a spectrum of co-mingled power structures. I believe J.C. … Continue reading.

There is a paradox here, because even as large long-cycle systems strongly affect our context, we also have a hard time observing these systems.  We can’t “see” a civilization.  “Seeing” large slow systems depend on the interpretation of diverse and diffuse evidence.  The intellectual capital[12]there will be much talk of capital later which lets us comprehend ecosystems is a cultural artifact.  Individuals within a sub-culture may reinterpret ecological evidence to fit their stories and beliefs[13]There is much recent consideration of confirmation bias as a human adaptation which can both stabilize and destabilize human systems.  How we think affects our ability to comprehend the ecological system we are standing in.  On the other hand, ecological systems don’t care what we are thinking about, only what we do.

If we want to be effective in the world we pay attention to what is going on around us.  If you want to cross a river, you pay attention to the current and the river bed[14]This is not an accidental metaphor, derived from the Chinese proverb shared with me by John Liu,  and I pick up the duality of recognizing both process and structure as a key part of design later.  In this way, we react in response to larger scale context.  In other words our context gives us purpose. However, these larger scale systems can only be altered by the cumulative effects of their smaller-scale evolutionary units (that’s us).  This is a paradox.  It suggests to me that there is a continuous and simultaneous flow of influence from large to small, and from small to large.  The influence from large to small is powerful.  We get this inheritance whether or not we like it.  On the other hand our ability as small things to influence to large, whether forest health or a nation state,  is not reliable, and so requires exceptional design, work, and adaptation over time.

“You don’t get to control what happens to you, only what you do about it” – The Random Factor[15]An old family friend changed her name to The Random Factor, and self published a book which discussed the phenomena of “resonance” which she described as the inexplicable reciprocal … Continue reading.

Scales in Ecological Systems

In ecological systems, communities of organisms are located in a particular physical position, within a physical landform like a ridge, valley, plain or plateau  [16]While I say communities of organisms there is a real and useful discussion here about competing theories of ecological assembly that argue over the existence of “communities”. I think … Continue reading.  These landforms can be organized into catchments and watersheds.  Watersheds come in all sizes from massive to tiny.  Watersheds either huddle within, or straddle, ecological regions, and climate zones.  When I go for a walk I can observe individual organisms in patches.  As I wander across a landform I can see patterns in the patches and how they sit in the landform[17]Precise definitions of landforms are provided by the science of geomophology and local analysis of landform is often more useful that global generalizations, for example Shipman’s Nearshore … Continue reading.  I can use remote sensing, aerial photography or maps to start understanding a watershed.  Through experience and research I can begin to understand ecological regions[18]for the purposes of stewardship planning, I believe the World Wildlife Foundation’s Terrestrial Ecoregions of the World is among the best complements to observation of raw temperature and … Continue reading.

Ecological systems are not just a random collection of elements, but rather large systems, like ecological regions, watersheds and landforms generate a set of dynamics that limit or organize all the clumps of organisms.  They define the problems we must try to solve, and so define our purpose.  In our model, I call these forces “keystone elements.[19]This concept is rough–but essentially, some common aspects of a system are more important than others, because they fundamentally structure smaller scale phenomena.  These elements may be … Continue reading.” These elements may include regular winter cold snaps, unpredictably long droughts, or the frequency of floods, in addition to biotic forces like beaver, or the moderation of climate and hydrology by communities of big old trees.  These keystone elements of our systems write the big stories of place, and each patch inherits that story because of our position within a layered ecological systems.

On the other end of the scale spectrum, within each place, a particular set of features or biota tell a stories about the unique qualities of that place.  These are “indicator elements”.  If you see a meadow of mountain sweet-cicely (Osmorhiza chilensis) and bedstraw (Galium arvense) among dwarf shrubs in a river floodplain it might suggest vegetation moderated by elk (Cervus canadensis) and flood.  The herbs are both weedy and travel by attaching to fur[20]This points toward another body of work focused on vegetation design around concepts of plant strategies, stress, disturbance, and the role of human work in changing the stress/disturbance mosaic, and the shrubs are dwarfed because of browse.  These indicator elements (weeds) help us understand the larger scale nature of a place because they are a responsive to the keystone elements (elk and flood).  If the story of elk is murmured and muttered over and over by indicators over a landscape, that is what leads us to identify elk as a keystone element of the ecological system, at the scale and cycle of the range and movement of the herd.

This interaction between large scale influences of climate and geology, and how survival strategies developed by organisms living in patches respond to these influences is the vast unfolding story of the evolution of life, which is our ultimate design context.

Scales in Human Systems

Human systems also structure and process over multiple scales.  Unlike ecological systems that organize around physical and biological processes, social systems organize around shared stories in human consciousness.  This may be what is most exceptional about humans–that we can create and sustain shared stories among vast populations that sustain collective behavior, sometimes in direct contradiction to ecological reality[21]A concept borrowed from Y.N. Harari’s Sapiens, which I enjoyed, even as his amateur evolutionary psychology is derided by students of human history, the vast majority of which had nothing to do … Continue reading.

We sustain and evolve our shared stories, in part, through institutions.  Not unlike keystone species, legal, religious, or economic institutions have complex influences that are inherited by a local human system.  We are born into institutions and may or may not be aware of their influence.  Like a Jay hiding nuts anticipating the depth of snow, we are conditioned and adapted to survive in the social system in which we are formed[22]This concept of “social niche formation” is reinforced by both inherited social institutions and built infrastructure..

In a landscape shaped by institutions, extended families and workgroups may develop a sub-culture.  A sub-culture is like an indicator species in an ecological system, telling a story of place–a social survival pattern in response to the disturbances and stresses of surrounding institutions[23]this reference to stress and disturbance is a second intentional reference to theories of ecological strategy and change including Competitor-Stress Tolerator-Ruderal (CSR) Theory and the Panarchy … Continue reading.  Sub-cultures form around shared stories, beliefs, rituals and taboos just as different species are varied in their physiological adaptations[24]This framework describing the four elements of culture came from Javan Bernakevitch at All Points Land Design.  Both institutions and sub-cultures reflect a history of human system evolution.  Just as in ecological systems, every structure tells a story of past processes.  Every cultural feature is a sign, like a bent branch or broken twig that marks a deer’s trail through the forest.

Not surprisingly, while ecological sciences are taught in most primary and secondary schools, we have no parallel curriculum about human systems.  They are hard to measure.  Experiments are difficult to control and repeat.  When we study human systems, we are both observer and observed.  A honest experimental construct can be laborious or even unethical to maintain.  Our stories about ourselves are more defined by institutions and subcultures than any empirical consensus on the human condition.  People get angry if you contradict their founding stories.

We are now at a point in history when big institutional relicts, like nation-states, monotheistic religions, and bank-debt currency systems dominate virtually every inch of the globe.  Even within our global cultures, there are still weakly influenced zones where unique local sub-cultures dominate: in rugged undeveloped landscapes, and in underground economies of decaying supercities[25]this is an admixture of observations by J.C. Scott mentioned above, on the global supremacy of grain-based empires, and the retreat of hill-peoples, combined with analysis by Y.N. Harari around … Continue reading.

Organizing Design over multiple Scales

If you begin to see the world as a nested, multi-scale interaction of human and ecological systems, it is easy to be overwhelmed.  Stewardship requires work.  The art and science of design helps us develop work that is well fitted to the design environment, both human and ecological, so that our actions resonate with the influences of larger scale phenomena, and are more likely to create cumulative effects that reflect our values.

Keyline design was such attempt to find order.  Percival Alfred Yeomans was an Australian mining engineer who envisioned what he called the “scales of permanence.”   His hypothesis is that when conducting a design you assess and integrate the hardest-to-change elements of a system first (like climate and landform), and work down into the smaller scale easier to change elements of a system (like where to put a fence).  In this way, your design features are well-nested within their context and serve many purposes.  Design begins with climate, landform and the organization of water, and only then do we locate roads, fencing and buildings. Secondarily, Yeoman’s offered us a clear sense of agency–that we are here to maximize the potential of the system, with a focus on water and soil to build the health and resilience of our community[26]Yeoman’s most complete presentation of his theories may be The Challenge of Landscape written in 1958.. Yeoman’s scales of permanence was birthed amidst Australian grazing operations, and even as I simplify his elegant system, the underlying strategy remains essentially unchanged[27]The most recent refinements of the keyline scales of permanence can be found in The Regrarians Platform, under the stewardship of Darren Doherty.

Yobarnie is a site developed for water retention and soil development in an Australian grazing landscape. (image: Water for Every Farm, P.A. Yeomans, 1966, www.Keyline.com.au, Photo: Douglass Baglin, 1964)

This concept is very similar in posture to another piece of work, on the other side of the globe, from roughly the same period of time by Fiebleman who coined his “theory of integrated levels” in which he suggested that our understanding of each scale (which he called levels), depends on our understanding of associated larger and smaller levels, and that unique properties emerge with each successive level.  In this way, both Yeomans and Fiebleman may have been indicator elements.[28]Interestingly both were individuals with professional land experience, who were trying to bring integrative thinking into ruling institutions during a period when knowledge in the academic world was … Continue reading.

Perhaps these principles of scale might apply to the design in human systems.  If so we would first considers and integrate the factors that most strongly shape local context, and are most difficult to change.  Only then can we effectively consider the opportunities for  interventions that might shape larger social patterns.  While this metaphor seems intriguing, how do we understand what aspects of human systems are most fixed and influential within a design environment?  What elements of our social system are “keystone?”

To have a purpose in a large system requires clarity about our personal values[29]I suspect this is perhaps Mollison’s greatest contribution to ecosystem management through his permaculture framework by demanding  ethical design first based on values rather than : care for … Continue reading.  As we work within our zone of influence, where we can have a discernible effect, we can see how our interventions might cumulatively affect larger scale patterns and systems, if they create synergy with our networks.  This aligns with the aphorism “think globally, act locally.”  A more detailed construction might be: “use your values to assess purpose from global to local, and then design interventions within local systems that are most likely to create cumulative global effects.”

A System at the Right Scale

A section of Puget Sound at 80k scale, with a pair of glacial plateau watersheds that drain to a culturally significant bay on the Tulalip Tribal reservation. A culturally and ecologically cohesive landscape.

The surrounding landscape at 320k scale with many jurisdictions, landforms, and levels of population density–likely inappropriate for development of stewardship systems.

Each design intervention occurs within a social-ecological system.  But practically speaking, how do we define the “system”?  The beauty of systems theory is that we can draw a box around a system at any scale we want, but not without consequence.  How we define our systems affects our ability to do work.  For stewardship, what matters is the work.  In short, the first step is to be somewhere.  Because multi-scale design in social-ecological systems is very difficult, but is almost impossible if you are not thinking about somewhere in particular.  It makes sense to make some kind of commitment to a place.

There are dangers in casting our systems too large.  Our governments profess to manage national or state systems.  Because these boxes are so large, we then divide our systems into topics, like flood, fish, farming, water supply, waste management, or transportation.  Different agencies are created to work on different topics.  In attempted efficiency, we assess and set policy at large scales, with little understanding of the interactions among topics or the particulars of neighborhoods.  A story that looks good on paper may hit the ground in unpredictable ways, destroying as much capital as it creates, and generating unintended consequences.

Stewardship is the antidote to the weakness of this centralized plan development and institutional policy deployment.  Stewardship revolves around something called a “place”.  Within a place, we have the opportunity to integrate institutions and sub-cultures for the purpose of structuring the human-ecosystem interface.  The various topics of government agencies can be reassembled back into an integrated whole[30]While I pass over this quickly, for those of us living in an industrialized empire, the challenge of reintegrating large institutional systems so they function well in a place may be a critical pivot … Continue reading.  Our places are both social and ecological, and so the definition of a place requires assessment of both ecological and human social systems.

What is the right scale to design stewardship?  If a design environment is too small, you will not be able to identify an intervention that has a cumulative effect in the ecosystem to achieve benefits only achieved at larger scales (for example recovery of a fish population).  If your intentions are too small compared to the influences at work at larger scales you reduce your ability to be effective (for example modest restoration in the face of climate change, or inadequate tinkering in the face of rapid immigration).  You can’t fix watershed hydrology on a single parcel.  You can’t shift government policy in one household.  This is not to discourage small scale moral action, but if we are designing effort in community, lets take aim at scale.

If your design environment is too large, you exceed your ability to take meaningful action that is responsive to the nuance of context.  You waste effort because your actions are too generalized, and poorly adapted to the landscape you are trying to affect.  You are easily overwhelmed by complexity, and unable to organize conflicting community needs and concerns into a mutually beneficial pattern.  The number of people you need to involve to create a socially durable effect becomes unmanageable at large scales.  Its easy to become lost or misguided.

Scale in ecological systems is largely a function of area, while scale in human systems in largely a function of population.  This is important because we are looking for a right scale of assessment and action, optimal for affecting the human-ecosystem interface.  Too small is ineffective, but too large overwhelms our capabilities.  this optimal scale must consider both the ecological and human scale of you system.  Thus the right scale for assessment and stewardship design may be smaller that ecologically appealing, as human population density increases.  However, our ability to effectively steward community and ecological capital is more likely to pay off through cumulative effects, rather than grandiose schemes.  [31]These hypotheses follow many influences from Kirkpatrick Sale‘s Human Scale, Shumachers’s Small is Beautiful, or Ignasi Ribo’s Habitat, all the way back to Greek debates around … Continue reading.

To make any sense of a design environment we must draw a box around a piece of the whole, and try to understand what is happening inside, and how it relates to the rest of the whole.  I’d propose that for the purpose of ecological stewardship, that this box surrounds something called a “place”, which is neither too big nor too small, with size driven by population, and boundaries defined by a mix of hydrology and community experience.  This size is particularly important because stewardship without work has no ecological meaning.  By actually doing the work, we learn a great deal about exactly what we need larger scales of social systems to do to support stewardship in a meaningful way.

Processes, Structures, and Emergent Functions

To understand a system, we can cut it into parts.  There are wet parts, dry parts, living parts, non-living parts, evolved parts and anthropogenic parts [32]I have become increasingly cautious in using the term nature or natural, as I find it imprecise.  I try to reserve the term “natural” for those elements of a system that are the result … Continue reading.  We can measure size and density and temperature.  We can count individuals and patches, and convert the structure of our system into data.  While structure is easier to measure, it is only a snapshot of the system.  We can dissect and measure the broken musical instruments on a stage, but never hear the orchestra[33]When I was younger I was impressed by, Masanobu Fukuoka, an agronomist who invented a form of natural farming,  and who made a strong critique of examining systems by dissection, from which I … Continue reading.

Systems are always cycling into something else, and the way that systems change are through processes.  Processes include flows, transformations, and fluxes[34]This three fold taxonomy of processes comes from Simenstad and others and is part of a body of “process-based” restoration analysis, often shaped by the interaction of multiple physical and biological processes.  Processes are described by observing the change of structures over time.  Processes within processes shape structure, but structure also shapes process[35]In Meadows’ seminal primer Thinking in Systems, she describes processes and functions as flows and stocks.  Some system mapping software describes edges and nodes.  Other system models use … Continue reading.

This interaction among processes and structures creates the phenomena we see around us.  These phenomena occur at all temporal and spatial scales[36]Or as they say in Star Trek and graduate school, “in space and time…”, and reoccur again and again: waves on a beach, the wetting and drying of soils, the accumulation of toxins in a food chain, daily rush hour, or the annual production of a vegetable grower.  We call these durable patterns of structures and processes by different names: functions, dynamics, or in the cases, when a dynamic supports the stable and repeated generation of something of value, we call it “capital”.

These terms–functions, dynamics and capital–each have different shades of meaning, but I suspect that many of the fundamental attributes are the same.  In the end, I suspect we should focus particular attention on forms of capital. These recurring elements of systems emerge from the interactions of processes and structures[37]Emergence describes a process by which complex systems generate phenomena that are not apparent within any one part.So when we examine a system we look for structures and processes, and pay particular attention to processes as a generative force.

There are millions of processes occurring simultaneously at all scales, but not all processes are created equal.  Some processes so strongly shape and sustain the structure of systems, that we make special note.  While we appreciate all processes, as designers we are looking for those processes that most strongly shape or limit the structure of ecosystems.  In doing so we can best refine our observations, and develop a stewardship strategy[38]I suspect there is a relationship between keystone processes and their scale of operation, such that larger scale processes equate with Yeoman’s higher scales of permanence, or … Continue reading.

Critical Ecological Flows

To understand a system we look for the processes that are doing the work to create and sustain important structures.  Work over time creates the desired future social-ecological state, which is the goal of stewardship[39]The importance of recognizing processes in system change is identified by many authors and among many diverse systems, including Meadows, Holmgren, Simenstad, and Hollings among others.  The beauty of process observation in ecological systems is that you can understand the dynamics of wildly different systems by looking at a few critical flows.  These critical flows can be identified in any ecology text, and include:

  • Energy, which flows from the sun as radiation, captured by plants and the mass of earth and water, and is then transformed again and again until lost to entropy as heat,
  • Rare Earths, or nutrients which are either gaseous or mineral, and mobilized by temperature, water, and light, and provide the scarce building blocks of the carbon-based compounds necessary for life, specifically: nitrogen, phosphorus, potassium, calcium, magnesium, sulfur and another dozen and a half rare elements,
  • Air, which along with water, provides a energy-driven circulation system by which heat energy and water vapor and even rare earths are distributed over the globe, and between oceans and continents.
  • Water, which is in continuous cycle from pool to pool[40]A pool refers to a structure, where flows accumulate, driven by solar evaporation, air circulation and gravity.

It is no coincidence that these four flows were identified by Greek philosophers as the building blocks of the cosmos.  Many scientists like to suggest that the four elements framework was discarded with the advent of elemental chemistry, only to come back around to the four elements in their conceptual modelling of ecosystems!  Standing in a tropical swamp, or a boreal desert, you can typically understand the fundamental dynamics of your system of interest by observing the flow of these “elements” at multiple scales.

Critical Flows in Human Social Systems

Compared to ecological systems, when we try assess human systems, we find ourselves relatively blind.  We don’t teach a cohesive framework for human systems in primary or secondary school.  Perhaps this is because the responsible adults spend their lives arguing around positions and policies, and lack a common framework for human system assessment.  There are many confounding issues, creating an obstacle to stewardship design.  Without an analysis of the processes and structures of human systems, we are only operating with half an understanding of the design environment.

As a restoration ecologist, I had no training in how to understand human systems.  My family sub-culture introduced me to Marxist theory, but failed to teach me about financial systems, or give me experience in dominant legal institutions.  In my youth, I was a student of astrology.  The beauty of astrology is that it offers a thousand-year-old framework for human system analysis through a direct extension of the Greek’s four elements model–an easy road map for a lost ecologist.  Astrological theory divides human systems into physical, intellectual, emotional and spiritual domains.

Later in life, with a little more experience, I stumbled into B. Guy Peters’ writing about policy alignment among social institutions.  He identified hierarchies, markets, and networks as three distinct mechanisms for building social relationships that lead to coordinated action.  Each mechanism varies in the durability and character of the relationships created.  Peters’ framework enhanced my observations and fit neatly into my astrological taxonomies.  The quid pro quo of markets was governed by earth, the networks of ideas ruled by air, and willful hierarchical control governed by fire.  However, the emotional world of water was absent in Peters’ framework–perhaps appropriate for an academic focused on the power systems of nation states.  I experience this emotional world as belonging.

Why wouldn’t human systems be governed by critical flows like ecological systems?  Could we equip ourselves, like ecologists, to understand any system in which we were standing by assessing a set of critical flows?  Could this help me navigate the design of stewardship systems?

Toward this end I have, for better or for worse, adopted an evolving admixture of astrology and contemporary policy analysis to frame my social systems.  Over a period of several years it still satisfies my needs:

  • Agency, is the flow wherein an individual cedes their agency to the will of another, often resulting in hierarchies.  I suspect it is important to pay attention not to the accumulator of agency, but rather the process by which an individual cedes their agency as the source of the flow, just like the sun is the source of energy.  Is not our will like a divine spark?
  • Ownership, is the understanding among peoples over who has the right, often transferable, to use a set of resources, often resulting in markets where value is exchanged.  It is important to recognize that even more than agency, defining and enforcing ownership systems is perhaps the essential purpose of states (which operate at large scales).
  • Knowledge is difficult to control because it travels from person to person, combining and recombining unpredictably, and moves through decentralized networks.  I have found information networks and nodes to be a critical tool for system design when you lack control over larger systems of agency or ownership.
  • Belonging, the missing ingredient of Peters’ policy framework, and the glue which draws people together around a common affection for each other and place, built of trust and reciprocity[41]My consideration of belonging continues to evolve, through fellow ecologist Kimmerer’s Braiding Sweetgrass, and Nenad Maljković’s recent essay on trust..

In this way any human might stand within a social systems, and by observing a set of key flows, discern some of the processes that drive system functions and forms of cultural capital.

Emergence and Forms of Capital

This brings us finally, long-way-round, to my stated purpose of assessment for stewardship design:

Stewardship is the process of developing and sustaining diverse forms of capital through the cultivation of effective individual actors within a nested human-ecological system.”

Capital historically refers to financial capital, including built assets like factories, traded among capitalists and forming the “means of production and distribution” that defines our industrial age.  The meaning of the term has evolved to include more sophisticated “human capital” as we started to invest more of the capabilities of institutionalized humans.   Finally we’ve begun assessing “ecological capital” as we ponder the economic feedbacks and full economic costs of resource extraction.  The colonial project is ending, as the serpent has found its tail.  Ecological revenue is now an economic factor, even if born by future generations at a discounted rate[42]This is a placeholder for economic valuation of ecological capital which is problematic in the deepest sense of the word.So “capital” has grown to encompass many “forms of capital” which together describe the stable generative functions of both ecological systems and social systems[43]As with the “ecosystem goods and services” language of the Millennium Ecosystem Assessment, there is a risk of misunderstanding the dynamics of systems by only valuing human services.  … Continue reading.

Within the last couple years I have encountered two groups both describing forms of capital[44]Ethan Roland and Gregory Landua ‘s Eight Forms of Capital, followed by Hallsmith and Lietaer’s Growing Wealth, and I offer them here as a loosely organized pile of overlapping phenomena.  Some forms of capital seem to only emerge at larger scales.  Some only emerge under a complex combination of circumstances, and some obviously relate to each other.  While I am using words I have gathered from others, I have added a few concepts of my own, focused on the emergent properties of large ecological systems.  These proposed forms of capital are my reinterpretations, as I play with observing capital in the systems I work.  There is no perfect framework only frameworks that serve different purposes imperfectly.  I want to test the language describing key system flows (agency, ownership, information and belonging) in the context of understanding the nature of capital.  Further, I also consider each form of capital as it might apply specifically the work of ecological stewardship.  From this perspective I’d suggest that these “forms” are not discrete but rather overlapping and interdependent, and represent a confluence of processes and structures, which become stable and generative.

I use the term capital very broadly, to encompass various forms of infrastructure, both built and living.  I find myself using the term infrastructure similarly with poor separation between the two terms.  Even as I might identify “infrastructure capital” following Hallsmith and Lietaer, I might turn and describe “cultural infrastructure” as social constructs that enable stewardship.  Capital must be constructed at a particular scale, for its dynamics can function fully.  A train track in not capital, as it only functions when it connects two stations that are placed within population centers.  In some cases capital serves as a keystone element creating purpose within its system.  In other cases capital serves as an indicator, a particular assemblage of resources responding to the demands of context.  Understanding the forms of capital in a system, as a pattern of keystone elements, indicators, institutions and subcultures may be the critical step in integrated system assessment.  Toward this end, it will likely be useful to understand capital as a emergent property of structures and flows–a dynamic of a system.  A form of capital creates a pattern among critical flows of systems.  From there we can diagnose the absence of capital, or design its regeneration.  Lets look at that list:

  • Cultural – an accumulated and shared body of stories, beliefs, rituals and taboos that enable groups of people to create value together.  Culture spreads through networks but creates belonging, which motivates us to give our agency to shared ends.  Undermining our analytical abilities, culture is nested within culture.  It seems likely that “cultural capital” is just an imprecise umbrella for all non-physical forms of capital.
  • Institutional – a kind of cultural capital where rituals and embedded into durable social structures, enabling more efficient mobilization of ceded agency.  What are the institutions in your system, and at what scale and in what domains do they operate?  By what flows do they sustain their structure?
  • Intellectual – a particular understanding built of multiple experiences that can be stored and taught enabling technology.  In what systems are our understanding of keystone elements and indicators stored?  How is intellectual capital created, maintained and spread?
  • Technological – a particular kind of intellectual capital which enables the conversion of material capital into infrastructure.  Within our pools of intellectual capital, how do we develop and distribute technologies that enable stewardship?
  • Experiential – the accumulation of experience within an individual, allows for that individual to apply skill to create value. What are the mechanisms by which individuals in the system can acquire experiences that build capital?
  • Social – a network of individual-to-individual relationships which creates the belonging and trust which enables people to work for each others needs, or pool resources to achieve common goals.  This capital appears to be an underpinning of a number of other forms of cultural capital.  What are the sub-cultural networks that generate social capital in your system?
  • Financial – the ability to aggregate ownership to achieve shared goals through the use of currencies, contracts, and shared ownership structures, largely mediated through monetary systems.  Local financial systems are shaped by larger scale patterns of ownership and scarcity.  What aspects of stewardship are valued by financial systems, and which are not?
  • Potential Exchange – is a particular admixture to financial capital which describes our ability to orchestrate desired outcomes through currencies and exchanges other than the global system of bank-debt currency.  What are the existing mechanisms of exchange other than money?  What are immobilized assets that don’t flow because there is no mechanism for exchange?  How do various fees and taxation drive economic activity towards bank-debt currencies?
  • Spiritual – A sense of personal belonging to the unknown elements of the universe which gives individuals the will to exercise their agency.  Spiritual capital seems to be built by experience and reinforced by institutional sub-culture.  What are the underlying beliefs that shape our relationship to the landscape?
  • Entrepreneurial – an emergent capital where a combination of capital enables individuals to pursue vision by reorganizing and creating new institutions.  This is another specialized capital that has to do with the mechanisms that enable individuals to take experiential capital and use it to evolve institutions.  This relates strongly to panarchy theory, and the tendencies for institutions to go through cycles of evolution and ossification[45]This whole concept of the timing of change in relation to the natural cycles of systems proposed under Panarchy will be brought up in part 2..  What are the mechanisms by which an individual can create new institutions that realize stewardship?
  • Landform – the innate potential of the shape of a landscape to create value through the capture and flow of sun, water, and nutrients, or the presence of rare earths, within a given climate.  What services does the landscape naturally produce that creates flows, both historically and currently?
  • Living – The stock of organisms in our system that we can use to meet our needs.  What are the goods and services that organisms in the landscape currently producing?  What organisms were once present but are now missing?  What are dynamics not supported by the existing assemblage?
  • Material – Tools, materials, and machines extracted from landforms and living capital that enable efficient production and distribution, and allow us to modify ecosystems to meet our needs.  What are tools that are available for stewardship: facilities, vehicles, hand tools, machinery with small and large engines?
  • Infrastructure – the organization of material and technological capital into larger scale systems that allow for the increased efficiency in the application of collective work.  What are the structures of the systems that enable transportation, waste re-circulation, information flow, social interaction, human health, water supply, and energy?  Is this the right list of infrastructures?
  • Ecological – the proximate organization of organisms into webs of relationships that produces resilient, low entropy systems that efficiently capture and use flows of water, nutrients and sun energy, while moderating climate.  How is the living capital productivity or resilience affected by patterns of disturbance, stress, dispersal, refuge, predation, or mutualism?
  • Evolutionary – the ability of living capital to evolve over time through ecological processes, thereby increasing ecological capital without human effort.  Where are genetic resources at risk from non-evolutionary selection? Where genetic exchange and natural selection processes are compromised?  What is the genetic state of the living capital which has co-evolved under human stewardship?

The art and science of stewardship is the process of tending and increasing these forms of capital within the systems in which we live.  It stands to reason that system assessment involves these steps:

  1. Inventory of the various forms of capital present in our systems and the interactions among forms of capital.
  2. Identifying where shortages of capital prevent the fulfillment of values either because of influences from larger scales, or insufficient mechanisms at smaller scales.
  3. Assessment of how social and ecological flows limit the development of desired capital at the right scale.
  4. Identifying the appropriate scale for the efficient development of capital[46]This rough outline is a simplification of Savory’s Holistic Management framework, as presented by Bernakevitch, and will be picked up again in more detail with designing stewardship system … Continue reading.
  5. Where is a system dependent on external flows to sustain capital functions?

This assessment for stewardship has value when it leads to effective action.  System assessment, informed by values, naturally beings to suggest weak links, and actions.  System assessments in the absence of values creates large bureaucratic reports that have no meaning.  Assessment of systems therefore hinges of values and what we hope to accomplish with our lives and our individual and collective agency.  An assessment can begin with an individual, but becomes much more powerful when it becomes a shared body of intellectual capital, and an ongoing flow of knowledge and belonging within a human system.  This said, I rarely share my assessment of capital at multiple scales with most of my partners in projects.  These are diagnostic frameworks, shadows of reality, that help the designer perceive, and ultimately distill an intervention, which must then be tested in reality.

I still hold out hope that we can build towards common understanding.  Stewardship enabled by cultural capital, rather than jury-rigged within a failing infrastructure. The challenge in operating at a meaningful scale is to build from individual agency to collective agency.  This requires shared values and a shared understanding of the systems in which we are working.  If we learn how to develop shared values that don’t distort our assessment of social and ecological systems, we may have a chance of getting where we want to go.

Intervention in the Zone of Influence

While much chatter is spent on large scale social and ecological phenomena (such as war, political contests and global crises) all these large scale dynamics are the expression of smaller scale dynamics which are shaped by large scale dynamics.  When we glimpse of the world at large, what we see is little more than what we have built through how we live our collective lives, as well as what we have inherited from our ancestors.  We may come to believe that the changes we desire are somewhere out there in that amorphous whole.  However, it is clear that our agency is local and immediate.  Our best information is local and immediate.  From an ecological perspective, we only belong to the land we stand on and the people we are standing next to.  The resources we actually have to work with are those in our hands.  Our ability to create cumulative effect is through organization of our zone of influence.

Design is the process of converting our values into the systems in which we live.  These systems are both social and ecological.  We use capital to build capital.  Capital is not created from nothing, but rather involves the reorganization of existing flows.  If we design our work well we become more effective in the future[47]The refinement of adaptive management theory by Snowden’s Cynfin Framework provides a useful method for adjusting our decision approach to the complexity found in systems..

The process of envisioning a desired future state starts with a reckoning of climate and geology, including the cultural climate, and dominant institutions in which we have been born.  Within that landscape we consider states, population centers and their institutions, as well as the flow of water, and recurring ecological keystone elements distributed among landforms.  While considering the flows of critical resources, created by this pattern, we can begin to inventory forms of capital, in both living systems, built environments, and ecological systems.  We compare this inventory of our capability to our values, and look for collective goals–what we want to build for the future.    This is the platform that may enable collective integrated design.  Any social-ecological vision is realized through a series of treatments and observations.  Each treatment changes the stocks of capital required to create and sustain our desired future state.  It begins with accurate assessment.  Then you act, and assess again.

Part Two

I am currently working on a complementary infographic and essay focused on the process of designing a social-ecological vision, and working toward that vision through a series of interventions and observations.

I am grateful for any insight or discussion, through the Ecosystem Guild and Restoration Camping facebook page.

FootnoteS

References

References
1 Different authors differ in their choreography of the dance, from Hollings’ early descriptions of adaptive management, evolved into the Open Standards for the Practice of Conservation parallel to Holmgren’s principle “observe and interact“.  Contextual variations are proposed by Snowden’s Cynfin framework.  The underlying pattern of observe and act and do it over again is the same.
2 A portion of my fascination with this work, and my approach, comes from playing the classical East Asian strategy game of Go.  Many complex games offer metaphorical guidance
3 Many strategic approaches depend on construction of shared models, such as Stroh’s Systems Thinking for Social Change, group exercises in Value Creation Chain evaluation proposed under Lean Management, or logic chain modelling in Open Standards for the Practice of Conservation.
4 This nomenclature for ecological processes is inspired by  processes-based models developed Simenstad and others, and will be revisited later, however the division of systems into four elements is ancient and informs the later discussion of system flows
5 “Ecosystem state” is common short hand for the structure of a system at a moment in time
6 I suspect that collective design capability is different than individual design capabilities and that individual design capabilities may not be sufficient to solve ecological stewardship problems.
7 The term “social-ecological system” has emerged in part form the adaptive management community described earlier, the subject of increasing scholarly work
8 This is not intended to suggest that when humans detach from evolutionary processes and systems that there are not consequences in our mental landscape.  We could likely describe a wildness gradient in human social systems as well as ecosystems.  Emerging rewilding communities are actively exploring these concepts
9 It is important to differentiate between work and talk.  It is the work that affects ecosystems, and the talk only counts when it changes the work
10 There is a feedback loop here, recently clarified by a colleague Joe Brewer, who introduced the concept of “social niche formation” whereby we create inherited infrastructures that guide future behavior without the need for conscious design.
11 While this is a flip generalization, it is also intended to point at a particular aspect of context.  Our social systems existing within a spectrum of co-mingled power structures. I believe J.C. Scott’s scholarly exploration of the historical relationships between grain-based empires and their peripheral decentralized hill-peoples is an important exploration of this dynamic with modern applications
12 there will be much talk of capital later
13 There is much recent consideration of confirmation bias as a human adaptation which can both stabilize and destabilize human systems
14 This is not an accidental metaphor, derived from the Chinese proverb shared with me by John Liu,  and I pick up the duality of recognizing both process and structure as a key part of design later
15 An old family friend changed her name to The Random Factor, and self published a book which discussed the phenomena of “resonance” which she described as the inexplicable reciprocal relationship between scales experienced in individual human lives. By doing so she planted seeds in my 12-year-old mind.  When you search google for the random factor and resonance, you find engineering parameters.
16 While I say communities of organisms there is a real and useful discussion here about competing theories of ecological assembly that argue over the existence of “communities”. I think there may be some metaphorical importance there.
17 Precise definitions of landforms are provided by the science of geomophology and local analysis of landform is often more useful that global generalizations, for example Shipman’s Nearshore Classification, Montgomery’s local stream classification strategies, or syntheses that connect river process to channel pattern.
18 for the purposes of stewardship planning, I believe the World Wildlife Foundation’s Terrestrial Ecoregions of the World is among the best complements to observation of raw temperature and precipitation data , and the earth as a whole.
19 This concept is rough–but essentially, some common aspects of a system are more important than others, because they fundamentally structure smaller scale phenomena.  These elements may be structures or processes, and physical or biological, or all of the above.
20 This points toward another body of work focused on vegetation design around concepts of plant strategies, stress, disturbance, and the role of human work in changing the stress/disturbance mosaic
21 A concept borrowed from Y.N. Harari’s Sapiens, which I enjoyed, even as his amateur evolutionary psychology is derided by students of human history, the vast majority of which had nothing to do with the dynamics of grain empires.
22 This concept of “social niche formation” is reinforced by both inherited social institutions and built infrastructure.
23 this reference to stress and disturbance is a second intentional reference to theories of ecological strategy and change including Competitor-Stress Tolerator-Ruderal (CSR) Theory and the Panarchy Hypothesis to be picked up again when we discuss stewardship design.
24 This framework describing the four elements of culture came from Javan Bernakevitch at All Points Land Design
25 this is an admixture of observations by J.C. Scott mentioned above, on the global supremacy of grain-based empires, and the retreat of hill-peoples, combined with analysis by Y.N. Harari around global systems of cultural homogenization.
26 Yeoman’s most complete presentation of his theories may be The Challenge of Landscape written in 1958.
27 The most recent refinements of the keyline scales of permanence can be found in The Regrarians Platform, under the stewardship of Darren Doherty.
28 Interestingly both were individuals with professional land experience, who were trying to bring integrative thinking into ruling institutions during a period when knowledge in the academic world was being balkanized into different specialized fields.
29 I suspect this is perhaps Mollison’s greatest contribution to ecosystem management through his permaculture framework by demanding  ethical design first based on values rather than : care for land, care for people, and return of surplus.
30 While I pass over this quickly, for those of us living in an industrialized empire, the challenge of reintegrating large institutional systems so they function well in a place may be a critical pivot point for our careening civilization, and in developing adaptive capacity within our institutions.  However our institutions do not typically recognize their weakness in places, or the opportunity for improvement offered by places.  I suspect different subcultures will increasingly define themselves by their attitudes about our increasingly incompetent institutions from Kaizen Gemba to nihilistic forms of anarchism.  I use the term “incompetent” here in a geomorphic sense, like a river that is not able to move its sediment.  Our institutions may be structurally unable to accomplish the purposes being required by ecological systems.
31 These hypotheses follow many influences from Kirkpatrick Sale‘s Human Scale, Shumachers’s Small is Beautiful, or Ignasi Ribo’s Habitat, all the way back to Greek debates around community size and structure.
32 I have become increasingly cautious in using the term nature or natural, as I find it imprecise.  I try to reserve the term “natural” for those elements of a system that are the result of evolutionary processes.  But are not humans and our regnerative and degenerative impulses not an acting out of evolutionary process?
33 When I was younger I was impressed by, Masanobu Fukuoka, an agronomist who invented a form of natural farming,  and who made a strong critique of examining systems by dissection, from which I gathered his broken instruments metaphor
34 This three fold taxonomy of processes comes from Simenstad and others and is part of a body of “process-based” restoration analysis
35 In Meadows’ seminal primer Thinking in Systems, she describes processes and functions as flows and stocks.  Some system mapping software describes edges and nodes.  Other system models use different labels like drivers, results, or outcomes, to describe the role of an elements within a logical chain of influences.
36 Or as they say in Star Trek and graduate school, “in space and time…”
37 Emergence describes a process by which complex systems generate phenomena that are not apparent within any one part.
38 I suspect there is a relationship between keystone processes and their scale of operation, such that larger scale processes equate with Yeoman’s higher scales of permanence, or Feibleman’s higher levels, and this logic may be useful in understanding the dynamics of human social systems.
39 The importance of recognizing processes in system change is identified by many authors and among many diverse systems, including Meadows, Holmgren, Simenstad, and Hollings among others
40 A pool refers to a structure, where flows accumulate
41 My consideration of belonging continues to evolve, through fellow ecologist Kimmerer’s Braiding Sweetgrass, and Nenad Maljković’s recent essay on trust.
42 This is a placeholder for economic valuation of ecological capital which is problematic in the deepest sense of the word.
43 As with the “ecosystem goods and services” language of the Millennium Ecosystem Assessment, there is a risk of misunderstanding the dynamics of systems by only valuing human services.  In addition Anand Giridharadas provides a robust critique of debating social justice without analyzing social systems, and his critique could extend well to an environmentalism that assumes extraction economies.
44 Ethan Roland and Gregory Landua ‘s Eight Forms of Capital, followed by Hallsmith and Lietaer’s Growing Wealth
45 This whole concept of the timing of change in relation to the natural cycles of systems proposed under Panarchy will be brought up in part 2.
46 This rough outline is a simplification of Savory’s Holistic Management framework, as presented by Bernakevitch, and will be picked up again in more detail with designing stewardship system interventions
47 The refinement of adaptive management theory by Snowden’s Cynfin Framework provides a useful method for adjusting our decision approach to the complexity found in systems.

Multiple Forms of Capital—Building Ecosystems Among Neighbors

Do all relationships hinge on money?  Obviously not.  But why is cash compensation so important in some partitions of life and not for others?  Do you need cash to help your grandmother?

Consider the dynamics of volunteer labor in the environmental sector.  Volunteer engagement is recognized as intellectually necessary, but not celebrated as efficient or effective.  Volunteer labor shows up unpredictably in three to five hour blocks.  We offer sub-optimal tools and set them to work wherever and whenever the money runs out.  Volunteers are often tended by a  high-turnover volunteer coordinator or intern.  Few shops invest deeply in the skills and knowledge of their communities and there may be little continuity between one experience and the next.  These dynamics are exacerbated by a system of distributed projects that arrive suddenly and then depart depending on grant availability.  Each such shop competes for a share of government appropriations which define the scope of their effort.  Each shop struggles between allocating labor to doing on-the-ground work , and grabbing and maintaining the attention of officials and funders.  Projects may not address root causes of ecosystem decline, or otherwise pour water in a leaking bucket.  We don’t expect landowners to be stewards, and most landowners don’t know anything about our watershed management.  Agency acquisition, and removal of people, is celebrated as the sure way to protect the landbase.

So in this system, who holds the watershed vision?  What does the community think about regulation?  Do their politicians and officials need to have a coherent ecosystem platform?

I am not interested in another environmental hierarchy, with a board and an executive, competing to get grants to pay staff to work another strategic plan.  This environmental project system is vital and full of good people doing good work–but it is not a system for empowering and building responsibility in community.  We talk about community engagement like a marketing campaign.  I am increasingly suspicious that we are missing the actual target.

We are focused on cash both because of a melange of social conditioning, and because our institutions punish those who don’t cleave to the written and unwritten rules of the competitive market.  But what is the necessary scope of ecosystem stewardship?  Where does this obligation to restore the watershed live?  Who understands enough to care?  What makes stewardship a living part of our culture?  How do we retain and maintain the flow of information?  How do stewardship skills pass from generation to generation?  Where are YOU responsible for?

We need to start playing the long game.

The Ecosystem Guild vision could be described as a union of ecosystem volunteers.  It is a egalitarian organization where members support each other in working towards shared goals.  We invest in our membership to increase our capabilities, because belonging and knowledge gives us strength. We negotiate more rewarding and durable relationships among guild members, ecosystems, and local recovery efforts.  We take apprentices, talk to new neighbors, and pitch in.  The power of our union comes from detailed local knowledge, and in creating mutually beneficial relationships so that all members are nourished.

This system has functions that are not yet present, to enable a reciprocal relationship among peoples and land, and a local reintegration of cash and non-cash economies around the management of the commons.  We have more financial capital than just about anywhere on earth, but we are still impoverished when it comes to ecosystem stewardship.

  • Social Capital – what makes humans powerful is our ability to sustain complex organizations and coordinate our labor.
  • Experiential Capital – the only way to act effectively in complex ecological system is to have the experience in those systems to see that pattern and design the intervention.
  • Intellectual Capital – as we work, we accumulate stories, measurements and concepts that we can give to others, to support our shared work
  • .Living Capital – the beauty of ecosystems is that they are self-replicating.  We can grow most of what we need to do ecosystem restoration and our campsites and old projects if well-designed become a resources.
  • Cultural Capital – the combination of our stories, rituals, taboos, and beliefs become the wellspring from which our children learn and act.
  • Material Capital – restoration camping creates a pool of shelter, technologies and tools that will serve us for restoration or for disaster relief.
  • Spiritual Capital – perhaps the greatest gift of restoring ecosystems is the connection to place, and to self and our many purposes that are far greater than the cash economy.

(This way of describing capital was borrowed from Ethan Rolland and Gregory Landua)

Our hypothesis is that a culture of stewardship will not emerge from a cash transaction (almost by definition!)  Stewardship revolves around personal relationship with place, and that this relationship is best defined in terms direct and tangible.  Stewardship capacity is build over time.  So we do what 300,000 years of humanity has done.  We take a piece of our short lives, and go tend to the ecosystem with our community.  By forming a union of stewards, we remove the inter-mediation of the agency and the non-profit, and instead of being pushed to do tasks of little consequence, we turn and pull the whole of society, industry, and government into the true generational work sitting right in front of us.