Showing posts with label relational values. Show all posts
Showing posts with label relational values. Show all posts

Tuesday, July 28, 2020

Author Contributions? Epic Fail, or Relational Success

By Kai Chan for CHANS Lab Views

This is (an extra) part of a series, How to Write a Winning Proposal—in 10 Hard Steps (why Author Contributions at the proposal stage? Because you need to think about these issues early: read on!)


Who did what? Who deserves the real credit, and who came along for the ride? Who contributed what %?

Author Contributions statements for papers, theses, and tenure files are far more important than they might seem. Writing these little statements well is also far more difficult than it appears. I learned this the hard way, with an epic fail at one of the most important junctures of my professional career.

This difficulty isn’t helped by understandable but mistaken notions that these statements are about the ‘real credit’ or percent contributions.

I was going up for promotion—a crucial moment in an academic’s career. My director, who had to write the crucial departmental letter that would accompany my file to the higher levels at the university, was also a coauthor on one of the articles I submitted. I was directed to write a statement clarifying my contributions to the papers. I interpreted it as “Show that this was mostly your work—that you brought the key ingredients, not your coauthors”. Error #1.

My director/coauthor flagged a concern. Ouch. I reread the statement to understand. It started with my contributions, and followed with my coauthor’s, almost as if these were an afterthought barely worth mentioning. I also averaged-up—that is, if I felt I did most of a task (e.g., designing the analysis), I assigned it to myself. E.g., “I designed and executed the analysis, I wrote the paper. My coauthor edited.” Now imagining my coauthor’s perspective, my heart surged, my face flushed, and shame and disgust washed over me. What I wrote wasn't false, but it was certainly not an equal representation of both sets of contributions. It oriented around mine, because that's how I understood the task (wrongly).

The irony was palpable. I had already become excited about relational values (preferences, principles and virtues associated with human relationships involving nature; see also here), and I had been consciously thinking relationally in general. That is, I had been thinking first about how actions reflected and built appropriate relationships, and only second how they yielded positive or negative consequences. Here, I clearly failed: I had unconsciously treated the authorship statement as a means to the end of impressing reviewers, entirely missing their crucial contributions to building or eroding the relationships I sought with cherished colleagues.

Ugh.

One might think, following such a teachable moment of shame, that I would have written flawless Author Contributions statements ever since. I wish I could say that were true. I don’t normally make the same mistake twice, but Author Contribution statements are full of ways to fail.

If we think of the hours spent directly on the manuscript,
we may think like this. But that doesn't tell the full story.


More recently, the same cherished coauthor and I were wrapping up a paper many years in the making (almost a decade). Finally, it was time to write an author contributions statement. I was conscious to err on the side of generosity. I listed our contributions together (not mine first). I emphasized shared contributions to tasks wherever it seemed appropriate. But by my recollection, I had approached my coauthor with the idea, and indeed, with a draft of what I felt we needed to say, and she had responded to that. So, I wrote something like, “KC wrote the first draft.”

It was déjà vu when my coauthor responded with edits and comments, with her recollection that we co-wrote the first draft. My coauthor pointed out that it had been her idea to include an empirical component at all. I had started counting ‘first draft’ from even before there had been an empirical component (which was now the central identity of the paper). The paper sure was different back then, without its central contribution. Point taken, absolutely we co-wrote the first real draft of the current paper.

Worse, though, my mind full of the many hundreds of hours that I spent coding papers and refining the analysis without troubling my coauthor, I claimed credit for designing the analysis. She contested that, politely and respectfully, as always. When I wrote the statement, I didn’t even remember that it had been my coauthor’s idea to do an analysis, and indeed that we had discussed some of the major codes right at the outset. It wasn’t a long, involved or contentious conversation, so it didn’t even spring to mind. But it clearly structured everything that followed.

Double ugh.

This time, I had been thinking consciously with the lessons from last time. I had thought I was being generous. But my thinking was skewed by my memory, which was rooted in hours spent and emotion-laden moments as indicators of contributions. Key structural conversations from many years ago were overlooked.

It’s so much easier to remember one’s own contributions than others. I think in our own minds, others’ contributions often become momentary guidance in a journey that we travelled mostly solo.

Subconsciously, I was thinking about percent contributions as hours spent on the paper. In contrast, I had consciously brought my coauthor on board because I knew that she would leverage countless hours of her reading and thinking of different but complementary literatures into a focused contribution on the manuscript. And I knew that this focused contribution might enable the paper to be rich and beautiful.

I’ve also had experiences on the other side, of course, because I think it’s hardest for students to see their supervisor’s contributions because they structure what follows. One wonderful student had joined me to do a project that I had envisioned well before the student’s degree. He had first written about my contributions as the same as other coauthors (e.g., editing drafts). These other coauthors were ones I had suggested as committee members, while helping this student envision what the project could look like and how it could make a great contribution to the literature and to problems that we both seemed to care about (based on his Critical Ingredients document). He didn’t mean to diminish my contributions, they just weren’t that visible to him, because they were so structural as to be part of the context.

I had another student—among the most principled, fairest people I know—who wrote that she ‘wrote the paper’. The paper was a Google doc with a bunch of notes when she invited myself and a coauthor in to give it structure, direction, themes, and relevant literatures. Yes, she typed most of the words, and of course she led the project and clearly deserves first authorship. But for me, ‘wrote the paper’ now means ‘gave shape to the main ideas in a complete good draft’.

The whole notion of percent contributions makes zero sense to me, even though it’s explicitly requested by some journals and grant agencies (others are more progressive, e.g., CRediT, the Contributor Roles Taxonomy). There is no single dimension by which one can measure author contributions on a paper. A paper should be more than the sum of the parts; coauthorship shouldn’t replace work, but rather shape the whole paper.

Coauthorship therefore shouldn’t be measured in time spent, but our memories lead us that way.

Good notes are crucial here, to record others’ contributions along the way. Then can we write Author Contribution statements that reflect how a paper is a beautiful symphony of ideas from a team.

A great strategy, which can avoid a lot of awkwardness, is to discuss or specify the responsibilities at the outset. Personally, I generally avoid pre-structuring contributions so as to maintain an organic adaptive process, but it’s great to discuss the options.

Then we can write statements that depict research as a deeply relational process, and which further build these collaborative relationships as being of more than instrumental value.


Creative Commons Licence
CHANS Lab Views by Kai Chan's lab is licensed under a Creative Commons Attribution-ShareAlike 4.0 International License.
Based on a work at https://chanslabviews.blogspot.com.

Friday, July 24, 2020

Distilling and discussing the IPBES levers & leverage points for transformative change

14 months ago 132 nations agreed upon the pathways to sustainability. 

   These are the Levers and Leverage Points of the @IPBES #GlobalAssessment 

   They are far more provocative than they seem. This new paper in People and Nature explains why: https://besjournals.onlinelibrary.wiley.com/doi/10.1002/pan3.10124

 


Several accompanying pieces make different points:

  1. Our blog response to Peter Bridgewater, handling editor at PaN.
  2. My story in The Conversation
  3. An IPBES podcast, which just aired on Wed.

 

Please share with potentially interested parties. If we’re going to re-orient societal efforts towards transformative change and sustainability, we will need agreement on how, and that it’s needed.

 

Why is this in People and Nature? As a Lead Editor, I have seen firsthand the excellent work done by my colleagues there. We are collectively working towards transformative change in academic publishing. It offers precisely what my coauthors and I sought: deep interdisciplinarity and consistently thoughtful reviewing and editing. Peter’s blog (above) offers a glimpse of how we were pushed in all kinds of productive ways. In a few weeks, I’ll also share a paper Terre Satterfield and I have been working on for 8 years, also in PaN.


Creative Commons Licence
CHANS Lab Views by Kai Chan's lab is licensed under a Creative Commons Attribution-ShareAlike 4.0 International License.
Based on a work at https://chanslabviews.blogspot.com.

Thursday, June 18, 2020

IPBES—An Inside Take (the Series)

By Kai Chan, a Coordinating Lead Author for the Global Assessment, Chapter 5.

IPBES (the UN's Intergovernmental Science-Policy Platform on Biodiversity and Ecosystem Services) is making waves in the arena of environmental science and policy, particularly that dealing with biodiversity conservation, ecosystem services, and the multiple values of nature. It is also somewhat of an enigma, especially for those who haven't participated yet in a formal role.

But if you work in environmental science and policy, you're sure to be confronted by a wide range of questions, including whether you should get involved in an assessment, task force or review process. You might also wonder how it works, how politics enters the process (or if it doesn't), what the assessments are useful for, and how to cite them.
The first IPBES Assessment was on pollination

This series of posts is based on an inside take from someone who has been involved in multiple work packages, starting with the Conceptual Framework, but also including the Global Assessment, and now also the Values Assessment and the (proposed) Transformative Change Assessment.

Let me be clear: this series of posts is not a set of advertisements for IPBES. I entered the Conceptual Framework process highly skeptical but wondering about the questions above, and how much value there is in engaging in this kind of international science-policy process. At the time (the beginning for IPBES), the only way for me to understand what IPBES was about was to get involved. I did, and I was not initially inspired to do more. In fact, I then figured it wasn't worth my while, but at least I knew why. But years later, as you'll learn in these posts, fate conspired to rope me in.

Moreover, I keep questioning deeply whether working with IPBES is the best use of my time (worth the opportunity costs), despite some important successes. Although I've been very frustrated at times (through no fault of the IPBES Secretariat—for whom I have tremendous respect—but rather due to the institutional constraints hard-wired into the organization), I'm increasingly convinced it is.

Here are the posts in chronological order:






Wednesday, March 14, 2018

Ecosystem Services and NCP: There’s Room for Both in a Bigger Tent

Part of a series of posts about IPBES (the UN's Intergovernmental Science-Policy Platform on Biodiversity and Ecosystem Services) and an inside look at its processes.
[The following is an edited synopsis of part of our longer official response on March 12 in Science about nature's contributions to people (NCP). Re: the original article, see this IPBES news item.]
Given that the Inuit have over 50 words for snow, how does an Inuit person translate a white skier’s question, “How’s the snow?” Without a precise mapping of terms, the translation is likely to include other dimensions of meaning, including the ‘positionality’ of the questioner (a white outsider) and the underlying purpose (recreating on Inuit territory). There is no way for any outsider’s language and concepts--e.g., about ecosystem services--not to suffer the same fate: they will both lose meaning that is crucial to locals, while also accruing conceptual baggage that may alienate them. A key point of the NCP approach is to explicitly recognize the legitimacy of a context-specific understanding, which defies the predetermined categorization that is so central to the ecosystem-services approach. And thus NCP is not merely political compromise but rather a broadening of epistemologies.
The snow allegory illustrates elements of the statement that “ecosystem services are NCP”: yes, ‘ecosystem services’ represents an important subset of ways of understanding nature’s diverse contributions to people. For some—including many social scientists and humanities scholars—there is hesitation or resistance to engage with ‘ecosystem services’, since the term comes with a conceptual baggage regarding the implicit assumptions and intended purpose. Not only is there the troubling connotation in the analogy of ecosystems as service-providers like factories (Norgaard 2010), but ‘ecosystem services’ has become associated at least partly with the notion of pricing nature so as to save it (Spash 2008; Dempsey & Robertson 2012; Crouzat 2018; Castree 2017). NCP represents a response, to broaden the tent by broadening the term.
Our promotion of NCP is no battle for territory: ecosystem services researchers should keep using that term, and we will too—in appropriate contexts. It remains in IPBES’ name, our job titles, and our explanations of who we are and what we do. It is perfectly functional for some audiences, and preferable for others—but not all (Fairbank 2010). In some other contexts, we will use NCP in order to intentionally signal an approach that explicitly invites and embraces diverse conceptions of nature and our relationships with it. This conceptual broadening is especially important when stakeholders do not accept the stock-flow metaphor associated with narrowing down nature to natural capital and all of its contributions as services (Chan et al. 2016; Pollini 2016; Pascual et al. 2017).
The issue is not whether the social sciences and humanities are represented in the field, but how visible and comfortable they are, whether there could be more, and if it would be productive. There are important social-science and humanities contributions in ecosystem services, and we have all intentionally strived to make more space for these (Chan et al. 2012; Martín-López et al. 2014; Pascual et al., 2014; Díaz et al. 2015; Berbés-Blázquez et al., 2016; Stenseke & Larigauderie 2017). But many review papers have found a narrow engagement of ecosystem services research with the social sciences (Liquete et al. 2013; Haase et al. 2014; Nieto-Romero et al. 2014; Chaudhary et al. 2015; Luederitz et al. 2015; Fagerholm et al. 2016). We know of many excellent social scholars who have been turned off by the term, and some who have engaged and have contributed importantly report a persistent queasiness (Satterfield et al. 2013; Satz et al. 2013).
We favour a big tent for this party that is research on nature’s contributions, and terms aren’t one-size-fit-all. Since many scholars report continued chafing with ‘ecosystem services’, despite our efforts to stretch it, we simply intend to provide a new term to invite a broader range of scholars and knowledge holders.

References:

Berbés-Blázquez, M., J. A. González and U. Pascual (2016). "Towards an ecosystem services approach that addresses social power relations." Current Opinion in Environmental Sustainability 19: 134-143. http://www.sciencedirect.com/science/article/pii/S1877343516300070
Castree, N. (2017). "Speaking for the ‘people disciplines’: Global change science and its human dimensions." The Anthropocene Review 4(3): 160-182. http://journals.sagepub.com/doi/abs/10.1177/2053019617734249
Chan, K. M. A., T. Satterfield and J. Goldstein (2012). "Rethinking ecosystem services to better address and navigate cultural values." Ecological Economics 74(February): 8-18. http://www.sciencedirect.com/science/article/pii/S0921800911004927
Chan, K. M. A., P. Balvanera, K. Benessaiah, et al. (2016). "Why protect nature? Rethinking values and the environment." PNAS 113(6): 1462–1465. http://www.pnas.org/content/113/6/1462.full
Chaudhary, S., A. McGregor, D. Houston and N. Chettri (2015). "The evolution of ecosystem services: A time series and discourse-centered analysis." Environmental Science & Policy 54: 25-34. http://www.sciencedirect.com/science/article/pii/S1462901115001239
Crouzat, E., I. Arpin, L. Brunet, M. J. Colloff, F. Turkelboom and S. Lavorel (2018). "Researchers must be aware of their roles at the interface of ecosystem services science and policy." Ambio 47(1): 97-105. https://doi.org/10.1007/s13280-017-0939-1
Dempsey, J. and M. M. Robertson (2012). "Ecosystem services: Tensions, impurities, and points of engagement within neoliberalism." Progress in Human Geography. http://phg.sagepub.com/content/early/2012/03/13/0309132512437076.abstract
Díaz, S., S. Demissew, C. Joly, et al. (2015). "The IPBES Conceptual Framework - connecting nature and people." Current Opinion in Environmental Sustainability 14(June): 1-16. http://www.sciencedirect.com/science/article/pii/S187734351400116X
Fagerholm, N., M. Torralba, P. J. Burgess and T. Plieninger (2016). "A systematic map of ecosystem services assessments around European agroforestry." Ecological Indicators 62: 47-65. http://www.sciencedirect.com/science/article/pii/S1470160X15006482
Fairbank, M., Maullin, Metz and Associates, and Public Opinion Strategies (2010). National public opinion research project, The Nature Conservancy.
Haase, D., N. Larondelle, E. Andersson, et al. (2014). "A quantitative review of urban ecosystem service assessments: Concepts, models, and implementation." AMBIO 43(4): 413-433. https://doi.org/10.1007/s13280-014-0504-0
Liquete, C., C. Piroddi, E. G. Drakou, L. Gurney, S. Katsanevakis, A. Charef and B. Egoh (2013). "Current status and future prospects for the assessment of marine and coastal ecosystem services: A systematic review." PLoS ONE 8(7): e67737. http://dx.doi.org/10.1371%2Fjournal.pone.0067737
Luederitz, C., E. Brink, F. Gralla, et al. (2015). "A review of urban ecosystem services: six key challenges for future research." Ecosystem Services 14: 98-112. http://www.sciencedirect.com/science/article/pii/S2212041615300024
Martín-López, B., E. Gómez-Baggethun, M. García-Llorente and C. Montes (2014). "Trade-offs across value-domains in ecosystem services assessment." Ecological Indicators 37, Part A(0): 220-228. http://www.sciencedirect.com/science/article/pii/S1470160X1300109X
Nieto-Romero, M, Oteros-Rozas, E., González, J.A. and B Martín-López (2014) Exploring the knowledge landscape of ecosystem services assessments in Mediterranean agroecosystems: insights for future research. Environmental Science & Policy 37: 121-133 http://dx.doi.org/10.1016/j.envsci.2013.09.003
Norgaard, R. B. (2010). "Ecosystem services: From eye-opening metaphor to complexity blinder." Ecological Economics 69(6): 1219-1227. http://dx.doi.org/10.1016/j.ecolecon.2009.11.009
Pascual, U., Phelps, J., Garmendia, E., Brown, K., Corbera, E., Martin, A., Gomez-Baggethun, E., Muradian, R. (2014). Social Equity matters in Payments for Ecosystem Services. Bioscience 64(11): 1027-1036 doi: 10.1093/biosci/biu146
Pascual, U., P. Balvanera, S. Díaz, et al. (2017). "Valuing nature’s contributions to people: the IPBES approach." Current Opinion in Environmental Sustainability 26–27: 7-16. http://www.sciencedirect.com/science/article/pii/S1877343517300040
Pollini, J. (2016). Construction of nature. International Encyclopedia of Geography: People, the Earth, Environment and Technology. D. Richardson, N. Castree, M. F. Goodchild et al, John Wiley & Sons, Ltd: 1-7. http://dx.doi.org/10.1002/9781118786352.wbieg0420
Satterfield, T., R. Gregory, S. Klain, M. Roberts and K. M. Chan (2013). "Culture, intangibles and metrics in environmental management." Journal of Environmental Management 117: 103-114. http://www.sciencedirect.com/science/article/pii/S0301479712006184
Satz, D., R. K. Gould, K. M. A. Chan, et al. (2013). "The challenges of incorporating cultural ecosystem services into environmental assessment." Ambio 42(6): 675-684. http://dx.doi.org/10.1007/s13280-013-0386-6
Spash, C. L. (2008). "How much is that ecosystem in the window? The one with the bio-diverse trail." Environmental Values 17(2): 259-284. http://dx.doi.org/10.3197/096327108X303882
Stenseke, M. and A. Larigauderie (2017). "The role, importance and challenges of social sciences and humanities in the work of the intergovernmental science-policy platform on biodiversity and ecosystem services (IPBES)." Innovation: The European Journal of Social Science Research: 1-5. https://doi.org/10.1080/13511610.2017.1398076

Wednesday, March 9, 2016

Contributing to the relational value concept: considering ecological relationships and interdependent values


In their most recent article, published in PNAS, Kai Chan and colleagues (1) propose that framing ecosystem values in terms of relationships can help unpack why we value nature and how research and policy might better reflect our values. In this this thought-provoking conceptualization, Chan and colleagues consider two primary types of relational values. First, they consider relationships between people and places; that people value specific places of meaning, not necessarily an ecosystem service in abstraction. Second, they consider relationships among people that are mediated by important places and ecosystem components. The relational values concept can be further enhanced, however, by including not only relationships among people and between people and the environment, but also relationships among different ecosystem components. Such ecological relationships go beyond bio-physical processes. I do not mean to evoke generic environmental interactions such as salmon needing cold water and therefore needing a forested watershed. This basic biophysical model is already captured in Chan and colleagues’ discussion of the “golden rule” in their policy application number four (i.e., care for your place may translate into care for someone else’s place if the two are ecologically connected). Rather, what I mean is that the values people place on connected ecosystem components are themselves interdependent.
This fuller picture of relational values is illustrated in how the Cree Canadian First Nations people manage their goose hunting. I was fortunate enough to spend several seasons living in the Cree community of Wemindji, in James Bay, Quebec, and to learned about goose hunting, an important subsistence and cultural activity (2). Hunting takes place in specific coastal marshes; but, prime locations change over time as the James Bay coast rises out of the Earth’s mantle having been depressed by the massive ice sheets that covered much of North America during the last glacial period (2, 3). The land is still rising to this very day, causing coastal marshes to dry up and new ones to form (2). Coastal marshes and prime goose habitats change rapidly, within the course of human lifetimes (4).
Cree hunters often invest significant amounts of energy to build soft infrastructure, such as mud dikes, to protect important marshes from drying up so that future generations can hunt (2, 4). Through intergenerational use, these marshes become imbued with history, culture, and identity and take on a value of their own (2). However, management decisions are influenced by ongoing environmental, social, and technological changes (2). Hunters may stop maintaining a marsh if, for example, geese change their flight paths and no longer visit an area (2). The marsh is still valued as an historic place that contributes to people’s identity (2).
The goose and the coastal marsh each have a value that is relational to specific Cree hunters, that cannot be reduced to one another or substituted, and that is interdependent. The relational values in Cree goose hunting involve social-social relationships (e.g., intergenerational use), social-ecological relationships (e.g., hunters valuing birds and certain marshes), and ecological-ecological relationships (e.g., spatial-temporal interactions between geese and marshes)[1] (Fig. 1). What we can learn from the Cree goose hunting example is how the values people place on certain ecosystem components are interdependent with values they have for other components.
Considering a wider array of social and ecological relationships helps flesh out the relational value concept. It can promote cross fertilization with other disciplines such as social network research, where social-ecological systems are conceptualized as networks with social-social, social-ecological, and ecological-ecological relations (6). Such collaborations will hopefully lead to theoretical and methodological advances that will help us achieve Chan and colleagues’ goal: a meaningful understanding of ecosystem services valuation that can better inform research and policy.
Figure 1. The values people place on certain ecosystem components are interdependent with values they have for other components. Valuation in Cree goose hunting involves social-social relationships (SS, e.g., intergenerational use), social-ecological relationships (SE, e.g., hunters valuing birds and certain marshes), and ecological-ecological relationships (EE, e.g., spatial-temporal interactions between geese and marshes). These relationships define a network of interdependent social and ecological units (red and green circles, respectively). Figure adapted from Bodin and Tengö (6).
 
Acknowledgments: I’d like to thank the CHANS lab for hosting my commentary and Kai Chan for editorial comments and advice.
Jesse Sayles is a postdoctoral fellow at the Climate Change Adaptation Research Group at McGill University. He does human-environment and sustainability research in costal and watershed systems. He is friends and colleagues with several CHANS lab members.
References:

1.            Chan KM et al. (2016) Why protect nature? Rethinking values and the environment. Proc Natl Acad Sci U S A 113:1462–1465.
2.            Sayles JS, Mulrennan ME (2010) Securing a Future: Cree Hunters’ Resistance and Flexibility to Environmental Changes, Wemindji, James Bay. Ecol Soc 15:22.
3.            Pendea IF, Costopoulos A, Nielsen C, Chmura GL (2010) A new shoreline displacement model for the last 7 ka from eastern James Bay, Canada. Quat Res 73:474–484.
4.            Sayles JS (2015) No wilderness to plunder: Process thinking reveals Cree land-use via the goose-scape. Can Geogr / Le Géographe Can 59:297–303.
5.            Peloquin C, Berkes F (2009) Local knowledge, subsistence harvests, and social-ecological complexity in James Bay. Hum Ecol 37:533–545.
6.            Bodin Ö, Tengö M (2012) Disentangling intangible social–ecological systems. Glob Environ Chang 22:430–439.


Photo: Canada Geese flying in Wemindji.
Source: Cree Nation of Wemindji online gallery.
http://www.wemindji.ca/gallery/local_photographers/pics16.jpg



[1] While the coast is likely always to be important, a new set of ecosystem relationships may also be emerging. Hunters increasingly travel inland and hunt at roadside gravel pits due to a combination of social and ecological changes that affect where geese go and the amount of time people have for hunting (5). Thus, for some hunters, these roadside areas may take on a different value in the future than they have had in the past.

Wednesday, September 4, 2013

IPBES: Intense Politics of Biodiversity & Ecosystem Services

Part of a series of posts about IPBES (the UN's Intergovernmental Science-Policy Platform on Biodiversity and Ecosystem Services) and an inside look at its processes.
My title renaming of IPBES (from the Intergovernmental Platform on Biodiversity and Ecosystem Services to Intense Politics of…) reflects the single biggest lesson from my trip to Cape Town for the Expert Workshop on the Conceptual Framework (for an intro to IPBES and this workshop, see my previous blog post). That’s not necessarily bad: it can be fun (like a chess game, as Unai Pascual said), and good work is possible (I think).
My home for more than two days looked like this: 
Vancouver via London to Cape Town = a long way

Politics entered from the get-go, in terms of who was in the room. I was surprised throughout the nomination process for the Multidisciplinary Expert Panel (MEP) that there were to be only five representatives from all of “Western Europe and Other States”, a group that includes Australia, New Zealand, the US, and Canada (there are also five representatives from Eastern European States). No one that I spoke to at the Conceptual Framework meeting could see much sense in this distribution, given the preponderance of expertise in that Western Europe and Other States group. Absolutely it makes sense to work towards a certain equity, but the current configuration seems to go way too far. For the Conceptual Framework (CF) experts (different from the MEP),
Lion's Head, from V&A Waterfront, Cape Town
the distribution followed expertise more


closely, but between the CF experts, the MEP, and the Bureau members, there were notable absences. E.g., not present were Hal Mooney and Walt Reid (prominent leaders of the Millennium Ecosystem Assessment), Dolf DeGroot and Bob Costanza (of the Ecosystem Services Partnership and key early work on ecosystem services), and Gretchen Daily, Steve Polasky, Taylor Ricketts, Peter Kareiva, Heather Tallis, Anne Guerry, etc. (of the Natural Capital Project). Maybe they declined to be nominated, but I found their absence interesting, even though there were lots of great people present. No doubt the composition of participants influenced the direction of the conversation, in many ways.
The figure produced by the Paris (precursor) workshop on 
the conceptual framework

The aforementioned politics introduces a certain tyranny of the minority whereby minority viewpoints are overrepresented and still benefit from the political shield/shelter of being minority views globally. E.g., “nature's gifts” and “nature’s favours” both gained entry into the CF figure in the edits following Figure 1 from the early 2013 Paris precursor workshop (see below, on the left, under “Nature’s Benefits …”). Both were intended as a parallel but more palatable alternative to ecosystem services--a concept that was deeply problematized due largely to its capitalist associations and which might have been excluded from the figure entirely, were it not entrenched in the name of IPBES. But Nature’s gifts and favours? Where was the problematizing of that? To me, 'gifts' connotes much more intentionality than does ‘services’. Such imagined intention of nature is quaint and perhaps also very useful in some contexts, but questionable as a more appropriate representation of reality. As if nature really intends to 'gift' most of what humanity derives from it. BUT of course not all of the diagram will speak to everyone, nor could it. The very purpose of the diagram is that it should represent multiple ways of knowing, not just one (obviously difficult in just one figure). Thus, even though I find it strange that the alternative to 'service' (critiqued in part because of the assumption that nature does what it does for us) is a pair of terms that strike me as even more problematic that way, I'm thrilled that the figure includes multiple metaphors for human-nature relationships (as colleagues and I called for here).
The draft figure circulated prior to the Cape Town workshop
Note that there’s no blame to any individual here: the point is that individuals are intentionally representing the perceived interests of others. It’s politics, implicitly infiltrating into the science: the figure in question was supposed to represent our best understanding of how social-ecological systems work, highlighting the bits pertinent to IPBES. I won’t go on about other telltale signs of the excessive influence of politics in this figure—you can have fun with that yourself. The point here is that it isn’t necessarily wrong for politics to enter in this way: if the figure is to be at all useful, it must speak to the way that people view the world, so this level of politics is essential.

Politics entered at a personal scale, too. In terms of the work we did in Cape Town, it really  
It mattered who found their way to Cape Town, 
and who didn't
mattered to be in the right room. And if you had a good idea, you knew or quickly discovered that you wouldn’t have the time to champion it solo, so you’d better work the room to find or build supporters in others. Most of this was tasteful, and simply a product of the apparent necessity; some of it made my mouth pucker.
Politics—some obvious and some buried well beneath the surface—entered prominently in terms of what appeared at the center of the diagram. We literally spent hours on this, with various parties considering how it would be viewed by various constituents. Some attendees were concerned that the diagram could never fly with “Institutions, decisions, and drivers” in the centre (as in the Paris figure), and preferred to keep them off to the side as in the pre-workshop figure, because a central role for institutions, etc., de-emphasized nature, nature’s contributions, and human quality of life. There’s no right answer here, obviously, but for me (and many others) a central role for institutions, decisions, and actions allowed the appropriate depiction of these things affecting everything else. And for me, misrepresenting that key dynamic would be letting politics have too strong a hold on the science. Others differ, and they’re entitled to that.
On a personal note, I wish that I’d had the patience and evenhandedness in Cape Town to express my opinions as I have above. In the meeting itself, I got caught up in the discussion, where political considerations and science were being conflated and confused, and I argued forcefully, inadvertently taking a centre role in a major dispute. The jetlag that left me near-sleepless surely contributed, but next time I’ll strive to keep a firm grasp on the distinction between the science and the politics.
Berta Martín-López and Unai Pascual at Kirstenbosch
Despite the politics, it seems possible to achieve useful gains. As I mentioned earlier, it seemed essential that IPBES provide guidance about values and valuation. As I’ve said countless times in talks with a slide titled “ES = E$?”, ecosystem services have been conflated with the valuation and commodification of ecosystems and ecosystem goods and services. And valuation is what decision-makers and practitioners seem to ask for when they think about ecosystem services. But too many think about valuation in a dangerously simplistic way, which is why IPBES has such an important role to play. I made this point in the CF workshop, and it was heard and embraced. As a consequence, I had an opportunity to work with a super group of folks, including Unai Pascual and Berta Martín-López (pictured below) on guidance for and from IPBES. This work, and the day I spent with Unai and Berta at the Kirstenbosch Botanical Garden were the highlights of my trip.

Kirstenbosch Botanical Garden, and Table Mountain



Will I continue to play a role in IPBES? That depends partly on whether they’ll invite me back! Which is by no means a certainty. ;) But it also depends on what comes of our efforts, how much survives through the even-more political processes at the MEP and Bureau. And the fate there can be understood as an indication of what’s possible and how well I played the game—so it seems like an appropriate deciding factor for future engagement.
What does this all mean for IPBES? With it’s own unique mixing of political considerations into the process and outcomes of scientific assessment, it’s going to be a trying but potentially fruitful process. To be frank, I am not hugely optimistic, but I am tentatively hopeful. With this window into the most recent IPBES workshop plus your own knowledge and experiences, what do you think?