Why Restoration?

Why Restoration?

 

Ecological restoration is an intentional activity that initiates or accelerates the recovery of an ecosystem with respect to its health, integrity and sustainability. And, Ecological restoration is the process of assisting the recovery of an ecosystem that has been degraded, damaged, or destroyed.

 

  • Details

    Why Restoration?
    By
    R. Eugene Turner
    Department of Oceanography and Coastal Sciences
    Louisiana State University
    Baton Rouge, LA 70803

    “That which is not good for the beehive
    cannot be good for the bees.”
    Marcus Aurelius; Meditations
    Book 6, section. 54.
    What is the use of a house if you haven’t
    got a tolerable planet to put it on?”
    Henry David Thoreau

     

    Definition: ECOLOGICAL RESTORATION
    “Ecological restoration is an intentional activity that initiates or accelerates the recovery of an
    ecosystem with respect to its health, integrity and sustainability. And, Ecological restoration is
    the process of assisting the recovery of an ecosystem that has been degraded, damaged, or
    destroyed.”
    Society for Ecological Restoration 2004
     
    “Why Restoration? Because, it must be done, it can be done, and it is being done;
    We can improve upon the quality and quantity of our efforts.”

     

    Restoration is an intentional and positive response to a tragedy and a dilemma, and a response
    that needs to be done. Restoration offers a response to the human-created tragedy of species loss,
    habitat destruction or damage and change; it respects our heritage, and offers a way of change for
    a better future. It strives to address the question: How does the same species, Homo sapiens var.
    politicus, var. domesticus, and var. economus, live in a world with at least the minimum needs
    for food and shelter and also with resources to nurture its existential and spiritual needs, which
    include the right of all life forms to exist? It respects two great lessons: (1) The great lesson of
    ecology that everything is inter-connected, and, (2) The great lesson of religions and spirituality
    to nurture our indestructible compassion for all life. The practice of restoration addresses the
    dilemma of how to learn about, develop understanding of, and work with those lessons; and its
    time has come.

     

    The Anthropocene
    Restoration is a response to the consequences of the fact that humans are a dominant
    biogeochemical and physical agent on earth. The cumulative effect of this development was so
    great that the present epoch is called the Anthropocene (Steffan et al. 2008). The Anthropocene
    began about 200 years about when humans earnestly succeeded in separating themselves from
    intimate contact with nature on a daily basis and had a cumulative impact at the global scale. Ask
    yourself: what your relatives did to find food several generations ago, then the next generation,
    and now? Today, most of us have little experience of how to squeeze milk from a farm animal, to
    grow crops, to harvest wild plants, or to build shelter. We can put our arms around most of the
    largest trees we see on a regular basis, if we see any, and wouldn’t spend the night outdoors
    without our cell phone or earplugs. Hurricane Katrina drove people from New Orleans to find
    refuge in Baton Rouge, where I live. Some of these people complained about the sound of
    crickets at night – What is that racket? Someone call the sheriff! They were not silly or
    unintelligent people; they were only people unaccustomed to the sounds of frogs and crickets at
    night. Some of the night sounds they may have been used to are the city sounds of gunshots, cars
    and trolleys, TV and music, but not the noise from animals in a pond ecosystem. Stars cannot be
    seen clearly because of light pollution. Over the last few hundred years our baseline experience
    with nature has shifted, and there is a disconnect with the reality of our several hundred thousand
    years of genetic inheritance.

     

    The transition to the Antrhropocene in the New World by the end of the 1800s was
    chronicled especially well in ‘The Earth as Modified by Human Action’ written by G. P. Marsh
    (1885). Marsh was a linguist fluent in 20 languages, ambassador to Italy and traveled widely. He
    could see the broad picture of change from an intellectual point of view, within cultures from
    personal contact, and in landscapes he visited. And changes were happening quickly for him. He
    saw the US landscape transformed radically: virgin forests were cleared, the newly-invented
    John Deere plows turned Big Bluestem prairies into farmland, and ecosystems became
    unsustainable or unavailable for the people of the First Nations. He clearly would have been a
    proponent of restoration as a logical next step in social development (“…Man, who even now
    finds scarce breathing room on this vast globe, cannot retire from the Old World to some yet
    undiscovered continent, and wait for the slow action of such causes to replace, by a new
    creation, the Eden he has wasted
    ” [Marsh, p. 228]).

     

    Indicators
    Some indicators of these changes and impacts are in Figure 1 (Steffan et al., 2008).

    • Vitousek et al. (1997) estimated that 25% of the CO2 concentration results from human actions, about half of the world’s freshwater supply is used, half of the nitrogen fixation is by industrial fixation of Nitrogen gas (an energetically-expensive conversion), that more than 20% of the plant species in Canada are invasive species, 20% of the bird species are extinct in the last 2000 years, and that more than 70% of the marine fisheries are fully exploited (Vitousek et al. 1997)
    • Seventy-nine percent of the Earth’s terrestrial surface is missing all the mammals presentcirca 1500 (Morrison et al. 1996).
    • One billion people are without safe drinking water and 2 billion are without proper sewage treatment.
    • Fifty-two percent of the land on the planet is disturbed land, meaning that it has lost part or
      all of its natural ecological functions. If we exclude the uninhabitable land, then the
      disturbed land is 75% of the planet.
    • The total land area is 148,939,100 km2 and there are 6 billion people (today). Thus the
      inhabitable land is 107 x 106 km2 and there are 1.78 ha (4.4 ac) for each person, and the population is growing. In 25 years or so, the area per person will be half that number (2.2 ac per person). How densely populated is your home town? Your state? Your neighborhood? Could you gather and manufacture or trade for all of your food, housing materials, gadgets, transportation, etc., on the average 4.4 acres (today’s average)?

     

    “An invasion of armies can be resisted, but not an idea whose time has come. “
    Victor Hugo

     

    Restoration has been done, is being done, and needs to be done
    Restoration became necessary when conservation was not enough, or was not successful and the
    passivity that lets natural restoration happen was insufficient. Successful examples of habitat
    restoration are now found throughout the world as personal or local restoration efforts have been
    transformed into national, and even international programs (e.g., Bernhardt et al. 2005; Falk et al.
    2006). This conclusion is evident in recent scientific publications, legislation and programs
    funded. For example, the United Nations is involved in restoring the marshes of southern Iraq –
    the 10,000+ year old home of the Ma’Dan or ‘Marsh Arabs’ (Thesiger 1964; UNEP 2001). The
    rationale for this restoration effort is largely based on a human rights issue – it is explicitly
    recognized that the Ma’Dan culture depends entirely on “their” wetland ecosystem. Coastal
    rivers and estuarine systems have been restored (e.g., Delaware Bay, Thames) and federal
    agencies were formed to restore soil (e.g., Soil Conservation Service in the 1930s). Restoration
    has, in other words, achieved political respectability at many scales, and represents a serious
    reversal of some social views – not that this is, at all, sufficient in a qualitative or quantitative
    sense. Restoration is found within the political jurisdiction that you live in – and it is one purpose
    of this class to uncover the details of that fact.

     

    Restoration requires resources, which means time and will and sometimes finances, and
    also legal authority. Society has some of the money (and fossil fuel) now. But in a few more
    decades, after more wars and wasted opportunities, we will have less discretionary funds — and
    more people. As non-renewable resources decline, our dependence on renewable resources
    increases. The time for doing something is now, when resources are available and the problems
    have not increased further.

     

    While scientific investigations have quantified some of the many impacts of the
    Anthropocene, the science of restoration is about sustainable systems. The science of restoration
    is, therefore, about making progress in addressing a partially-identified problem with a very
    applied sense of value. Its value is immediate, applicable to many, and is long-lasting. It deals
    with the forces that have driven the equilibrium of pre-Anthropocene environments towards
    undesirable outcomes (humans now and later; other species). It may seem like a thick, unwieldy,
    and imponderable set of immense problems. But, unlike the drivers of the present outcomes,
    working out the new equilibrium is more forward-looking, intentional, and gives a chance to
    implement goals now, rather than later. Restoration has, therefore, a hopeful view that is one of
    reconciliation. We have significant choices remaining to ignore or embrace regarding species
    composition, exploitation, respect for future generations, governance, etc. …. Or not. One thing
    is for sure….. passive engagement is a choice for business as usual.

     

    The need for restoration expertise
    An analogy for restoration managers and scientists:
    Suppose that the electricity in a meeting room stopped, and then the electricity in the entire
    building was no longer in service. The air conditioner does not work, it is getting hot, and you
    take off your outer garment or tie to be cooler. The few windows are opened, but the alignment
    of the building is not meant for cross-ventilation and the small breeze through the room is
    insufficient to compensate for the heat generated by the people in it. The food in the refrigerator
    is starting spoil – the ice cream is melting. The cooks cannot cook, and the elevators do not
    move. The talk that you traveled a day to get here for is soon to be canceled if the system is not
    fixed. What do you do? Who do you call? — a plumber, a lawyer, or an electrician? You will
    seek the help, of course, of an electrician – someone with the expertise to match the identified
    problem. It would be good if they were known for doing fine professional work and that they had
    access to the proper repair tools, and that the specialist learned by apprenticeship working with
    another specialist, rather than from his cousin Jimmy “hip bop”, the car mechanic. But (s)he
    cannot complete job without someone to unlock the doors to the fuse box and they will get here
    sooner and fix it faster if they know the local building codes and construction methods. After the
    immediate problem is fixed, people might reasonably wonder about longer-term issues
    concerning this building or the next meeting. How many times is this going to happen again?
    Can we learn from this? What do we want the next meeting place to look like? How should it be
    designed? Who needs to be involved in constructing it? And, importantly, will it be sustainable?

     

    Scientists guide many environmental restoration efforts through direct involvement in a project,
    or indirectly through the incorporation of research results and development of ‘best management
    practices’, empirically defined outcomes and predictions, or even theoretical constructs. Their
    (our) progress in these endeavors has been non-linear and embedded with obstacles. There have
    been twists and turns in the priorities, methods, and perceived factual basis for conclusions. The
    generalizations about restoration trajectories among and within ecosystems have been sparse.
    Because the science of restoration is so young, we should not have expected anything but this
    result. The practice of restoration is not yet the same as when building a bridge that taxpayers
    cross daily, whose weight, structural integrity, and load capacity, etc., are well-defined in
    manuals and textbooks used in hundreds of classrooms. Although habitat restoration is supported
    by individuals and public entities, it is clear that there is also much to learn that would help meet
    the stated and un-stated objectives.

     

    Restoration, to be successful, also requires the meaningful metrics of success and an
    informed view of how to achieve success. We should not claim success if we don’t measure
    success and don’t have metrics that mean something – in the ecological sense. And the path to
    success requires practice. In that sense the practice can inform ecologists about issues not related
    to restoration. So it is a two-way communication between theoretical and applied science (Falk,
    Palmer and Zedler 2006).

     

    Restoration is more than science, management or applied science
    Scientists and managers have a job to do for a crowded planet. Restoration requires expertise to
    potentially do it right (Box 1). We must have technical skills, absolutely. – but, we must also be
    invited to participate and we need equipment and supplies and assistance. Even without
    adequate external help, our profession has some essential capabilities that are within our sphere
    of influence to sustain, and even improve. These possibilities mostly involve our
    professionalism. An essential one is that we need to learn from one another – which is one
    purpose of this class. Take risks and ask for opinions from others, identify what is needed, and
    seek out the uncertainties even when success looks unlikely, and consider speaking up (politely)
    when questions need to be asked – others probably have similar questions, but are too shy to ask.
    If we do this then maybe we can more often identify potential problems with the circuitry before
    a fuse blows or before the power is cut off, and repair problems quickly, so that the flow of
    energy continues in a sustained way to benefit everyone in the room.

     

    Goals
    Restoration ecology pulls together a wide range of ecological activities.
    – It challenges conservationists to shift from protection to the longer-term goal of
    restoring the whole ecosystems and society.
    – Applied ecologists are challenged to de-emphasize manipulation of single components
    of ecosystems and shift attention to the entire ecosystem.
    – Theoretical ecologists are challenged to develop practical tools to guide restoration and
    the indicators to monitor its success.
    Three goals are possible:
    1. To repair biotic communities.
    2. To re-establish biotic communities on the same sites if they are destroyed.
    3. To construct synthetic communities elsewhere if the original site is no longer
    an option.
    4. To have meaningful participation of society

     

    It is going to take a long, long time to accomplish this. The disturbance of terrestrial soils 200
    to 2000 years ago is evident today (Walters and Merritt 2008; Dupouey, et al. 2002). So let us
    begin now!

     

    References
    Bernhardt, E. et al. (and 24 co-authors) 2005. Synthesizing U.S. river restoration efforts. Science
    308: 636-637.
    Dupouey, J. L., E. dambrine, J. D. Laffite, and C. Moares 2002. Irreversible impact of past land
    use on forest soils and biodiversity. Ecology 83: 2978-2984. (PDF file)
    Falk, D.A., M. A. Palmer and J. B. Zedler 2006. Foundations of Restoration Ecology. Society for
    Ecological Restoration International, Island Press. 364 pp.
    Foster, D., F. Swanson, J. Aber, I. Burke, N. Brokaw, D. Tilman and A. Knapp 2003. The
    importance of land-use legacies to ecology and conservation. BioScience 53: 77-88.
    Hannah, L., D. Lohse, C. Hutchinson, J. L. Carr, and A. Landernai 1994. A preliminary
    inventory of human disturbance of world ecosystems. Ambio 23: 246-250.
    Marsh, G. P. 1885. The earth as modified by human action: A last revision of man and nature.
    Charles Scribner’s & Sons. New York:
    Morrison, J. C., W. Sechrest, E. Dinerstein, D. S. Wilcove, and J.F. Lamoreux 2007. Persistence
    of large mammal faunas as indicators of global human impacts. J. Mammology 88: 1363-
    1380.
    Shepard, P. 1996. The Only World We’ve Got : A Paul Shepard Reader. San Francisco; Sierra
    Club Books.
    Steffen, W., P. J. Crutzen and J. R. McNeill 2008. The Anthropocene: Are humans now
    overwhelming the great forces of Nature? Ambio 36: 614-621.
    Vitousek, P. M., H. A. Mooney, J. Lubchenco, J. M. Melillo 1997. Human domination of earth’s
    ecosystems. Science 277: 495-499.
    Walter, R. C. and D. J. Merritts 2008. Natural streams and the legacy of water-powered mills.
    Science 319: 299-304.

     

    Related readings
    Abram, D. 1996. The Spell of the Sensuous. Random House, Inc. New York. Chapter 1.
    Benayas, J. M. R., A. C. Newton, A. Diaz and J. M. Bullock 2009. Enhancement of biodiviersity
    and ecosystem services by ecological restoration: A meta-analysis. Science 325: 1121-
    1124.
    Demenocal, P. B., E. R. Cook, D. Demeritt, A. Hornborg, P. V. Kirch, R. McElreath, and J. A.
    Tainter 2005. Perspectives on Diamond’s collapse: How societies choose to fail or
    succeed. Current Anthropology 46: S91–S99.
    Ellis, E. C. 2009. Earth science in the Anthropocene: New epoch, new paradigm, new
    responsibilities. EOS 90: 473.
    Foster, D., F. Swanson, J. Aber, I. Burke, N. Brokaw, D. Tilman and A. Knapp 2003. The
    importance of land-use legacies to ecology and conservation. BioScience 53: 77-88.
    Jackson S.T. and R. J. Hobbs 2009.Ecological restoration in the light of ecological history.
    Science 325: 567-569.
    Kareiva, P. 2008. Ominous trends in nature recreation. Proceedings Nat. Acad. Sci. 105: 2757–
    2758.
    Nagarajan, P. 2006. Collapse of Easter Island: Lessons for Sustainability of Small Islands. J.
    Developing Societies 22: 287-301
    Rick, T. C. and J. M. Erlandson 2009. Coastal exploitation. Science 325: 952-953.
    Turner, R. E. 2005. On the cusp of restoration: Science and society. Restoration Ecology 13:
    165-173