Discursive Ecologies and the Problem of Environmental Meaning:

Toward a Post-Structural Ecolinguistics of Bricolaged Signification

This post advances a theoretical intervention in ecolinguistics and philosophy of language by challenging the assumption that environmental discourse is primarily narrative, representational, or metaphorically structured. Instead, it proposes the concept of discursive ecologies: dynamic, heterogeneous systems of signification through which ecological reality is continuously produced, stabilized, and destabilized.

Drawing on Arran Stibbe’s ecolinguistics, Thomas Kuhn’s paradigm theory, Claude Lévi-Strauss’s notion of bricolage, Michel Foucault’s discourse/power framework, and Jacques Derrida’s différance, the paper argues that industrial environmental language is not a coherent ideological system but a bricolaged assemblage of epistemically incompatible sign regimes. These regimes are stabilized not by semantic coherence but by institutional repetition, administrative embedding, and algorithmic reinforcement.

The central claim is that ecological meaning is not representational but procedurally generated within discursive infrastructures that pre-structure what counts as “nature,” “crisis,” and “solution.” Consequently, ecological breakdown is not only material but also a breakdown of epistemic intelligibility.

1. Introduction: Against Representation in Environmental Discourse

Contemporary ecolinguistics has demonstrated that language does not merely reflect ecological reality but shapes it through framing, metaphor, and narrative structure (Stibbe, 2015). However, dominant approaches remain implicitly representational: they assume that “stories” or “frames” correspond to underlying ecological conditions that can be more or less accurately described.

This post challenges that assumption.

It argues that environmental discourse does not operate primarily through stable narrative structures but through discursive ecologies, open, shifting systems of meaning in which ecological “objects” are effects of linguistic and institutional practices rather than pre-existing referents.

Accordingly, terms such as “climate change,” “sustainability,” or “natural resources” do not denote stable entities. They function as epistemic nodes within heterogeneous systems of signification, where meaning is continuously produced rather than represented.

This shift requires moving beyond narrative analysis toward a philosophy of language that foregrounds instability, power, and epistemic construction.

2. From Narrative to Discursive Ecology

Narrative-based ecolinguistics presupposes bounded structures: stories with coherence, sequence, and thematic unity. Yet environmental discourse is not organized through singular narratives but through overlapping, fragmented, and often contradictory systems.

We propose the concept of discursive ecology to capture:

the multiplicity of competing sign systems
the absence of global coherence
the continuous recombination of linguistic fragments across domains

Environmental meaning emerges not from unified storytelling but from interactions between institutional, scientific, economic, and algorithmic discourses.

Thus, ecological language is best understood not as narrative but as emergent system of distributed signification.

3. Ecolinguistics and Its Implicit Semantic Realism

Ecolinguistics, particularly in Stibbe’s formulation, introduces a normative distinction between “life-supporting” and “life-diminishing” stories. While analytically productive, this framework retains a form of semantic realism: it assumes that discourse can be evaluated against relatively stable ecological conditions.

This paper departs from that assumption by arguing that ecological “conditions” themselves are discursively mediated constructs. What counts as “damage,” “risk,” or “sustainability” is not externally given but produced within historically specific regimes of knowledge.

Ecolinguistics thus requires theoretical supplementation from post-structural philosophy of language.

4. Kuhn: Paradigms and Epistemic Closure in Environmental Rationality

Kuhn’s concept of paradigms provides a structural account of how knowledge systems stabilize meaning by excluding alternatives.

Applied to environmental discourse, the industrial paradigm determines:

what counts as ecological “problem”
what counts as legitimate “solution”
what remains epistemically invisible

For example, “growth” functions not as a hypothesis but as a paradigmatic precondition of intelligibility.

Ecological crisis, in this view, signals not merely empirical failure but paradigm-internal exhaustion: the inability of a conceptual system to accommodate its own anomalies.

5. Lévi-Strauss: Bricolage as Structure of Environmental Rationality

Industrial environmental discourse is not unified but structurally heterogeneous. Following Lévi-Strauss, it can be understood as bricolage: the construction of meaning from pre-existing conceptual fragments.

These fragments include:

theological teleologies (progress, salvation)
mechanistic metaphors (systems, inputs, outputs)
economic rationalities (efficiency, capital, optimization)
scientific formalism (modeling, equilibrium, prediction)

Crucially, these elements are not epistemically compatible. Yet they are continuously recombined into functional institutional discourse.

This implies that environmental language is not logically coherent but structurally assembled from heterogeneous semantic materials stabilized through institutional practice.

6. Foucault: Environmental Discourse as Power/Knowledge Formation

Foucault’s theory of discourse allows us to understand environmental language as inseparable from governance.

Contemporary ecological discourse operates through regimes such as:

carbon accounting systems
sustainability metrics
environmental risk modeling
net-zero governance frameworks

These do not merely describe ecological reality; they actively produce it as a governable object.

Thus, ecological knowledge is not external to power but is a product of power-knowledge formations that define what counts as environmental reality in the first place.

Environmental discourse is therefore a technology of legibility and control.

7. Derrida: Différance and the Non-Presence of Ecological Meaning

Derrida’s theory of différance introduces a fundamental instability into environmental signification.

Key ecological terms derive meaning only through differential relations:

nature vs culture
growth vs decay
sustainability vs collapse

However, these oppositions are never stable. Meaning is always deferred across chains of signification.

Thus:

ecological meaning never attains presence; it circulates through structural deferral.

“Nature” is not a referent but an effect of differential relations within discourse.

This destabilizes any assumption of direct linguistic access to ecological reality.

8. Discursive Ecology as Distributed Semiotic System

Integrating the above frameworks, we define discursive ecology as:

a distributed system of heterogeneous signifying practices through which ecological reality is continuously constructed, stabilized, and disrupted.

Within this system:

paradigms constrain intelligibility (Kuhn)
discourse organizes power (Foucault)
meaning is structurally unstable (Derrida)
systems are assembled from fragments (Lévi-Strauss)
and evaluative ecolinguistic judgments remain contextually situated

Environmental discourse is therefore neither unified nor representational but emergent, unstable, and structurally composite.

9. Algorithmic Mediation and the Reinforcement of Discursive Inertia

Digital language systems introduce a new layer of epistemic reinforcement.

Large-scale language models and predictive systems:

reproduce statistically dominant collocations
stabilize high-frequency metaphors
reinforce institutional discourse patterns

This produces a feedback loop in which dominant environmental framings are continuously amplified.

As a result, discursive ecology becomes increasingly self-referential, with reduced capacity for conceptual divergence.

This may be understood as algorithmically mediated epistemic closure.

10. Theoretical Implications for Linguistics and Philosophy of Language

This intervention challenges three dominant assumptions:

(1) Representationalism

Environmental language does not represent ecological reality but participates in its construction.

(2) Semantic stability

Key ecological terms do not have fixed meanings but operate through differential and deferred relations.

(3) Discursive coherence

Environmental discourse is not a unified ideological system but a bricolaged assemblage of heterogeneous epistemic fragments.

Together, these claims require a shift from narrative and metaphor analysis toward a post-structural philosophy of ecological language.

11. Toward a Non-Representational Ecology of Language

This post has argued that ecological discourse should be understood as a discursive ecology rather than a system of representation.

By integrating ecolinguistics with Kuhnian paradigms, Lévi-Straussian bricolage, Foucauldian power/knowledge, and Derridean différance, we have shown that environmental meaning is:

structurally unstable
institutionally produced
epistemically constrained
and semiotically deferred

The ecological crisis is therefore not only material but also a crisis of meaning-production: a breakdown in the discursive infrastructures through which ecological reality is rendered intelligible.

Future research in linguistics and philosophy of language must move beyond representation toward a theory of ecological semiosis as a distributed, unstable, and power-saturated process.

Sources

Foucault, M. (1972). The Archaeology of Knowledge.

Derrida, J. (1978). Writing and Difference.

Kuhn, T. (1962). The Structure of Scientific Revolutions.

Lévi-Strauss, C. (1966). The Savage Mind.

Stibbe, A. (2015). The Stories We Live By.