Chapter 2: Theoretical Foundations: Value Chain Governance, Industrial Upgrading, and the Green Capability Turn

In 2001, a European retail buyer visited a cluster of furniture manufacturers in Beijiao, Shunde District, Guangdong, carrying a forty-page questionnaire. It asked about formaldehyde emissions from panel board, VOC content in finishes, labor hours embedded in each container, and chain of custody for timber. Most factory owners in Beijiao had built their businesses on price. They could quote a per-unit cost to the yuan. They could not answer the questionnaire. Within two years, the buyer had shifted orders to factories in Vietnam that could.

Beijiao is not typical of Chinese furniture manufacturing. It is not even common. But it is real, and it exposes a fault line running through the global value chain literature: the difference between firms that occupy a position in a chain and firms that govern their own position within it. The first group responds to requirements. The second anticipates them, and occasionally shapes them.

This chapter builds the theoretical foundation for understanding that difference as it applies to environmental performance. The argument moves through three bodies of literature—value chain governance, industrial upgrading, and the resource-based and institutional theories of the firm—and proposes an integrated framework, the green capability turn, to explain why some firms convert regulatory pressure into competitive advantage while others convert it into nothing more than a cost line. The framework organizes evidence rather than forecasting outcomes; the chapters that follow test it against cases from Chinese manufacturing.

2.1 Value Chain Governance: From Hierarchy to Network

2.1.1 The Governance Puzzle

A factory in Dongguan assembles circuit boards for a German automotive supplier. It does not operate in a market. It operates in a relationship. The German firm specifies the solder alloy, audits the reflow ovens, trains the line supervisors, and sets the defect tolerance at four parts per million. The Dongguan factory cannot sell the exact board it makes for this customer to anyone else, and the German firm cannot instantly switch to another supplier without requalifying the entire production process. Neither party owns the other. Neither is truly independent. Value chain governance theory exists to explain this puzzle: how economic activity is coordinated across firm boundaries without the visible hand of ownership or the invisible hand of spot markets.

Gereffi, Humphrey, and Sturgeon (2005) answered with a framework that remains the field's most cited. Governance structures vary along a spectrum defined by three variables: the complexity of information exchanged, the codifiability of that information, and the capability of suppliers to meet buyer requirements. Where information is complex and difficult to codify, and where supplier capability is low, lead firms must exercise close control—through vertical integration (hierarchy) or through "captive" relationships in which suppliers are tightly monitored and heavily dependent. Where information is simple and codifiable, and suppliers are capable, transactions can be governed by price (market governance). Between these poles lie modular, relational, and captive forms, each with its own logic of coordination and its own implications for how firms learn, upgrade, and respond to new demands.

The framework has been criticized for what it leaves out. Gereffi et al. acknowledged that governance is not fixed: a relationship can move from captive to relational as supplier capability grows, or from modular to captive as buyer requirements tighten. The framework describes a snapshot, not a trajectory. It also treats "lead firm" as a unitary actor, when buying decisions are made by teams with different priorities—compliance officers, sustainability managers, procurement directors—who often disagree with one another. And it was built primarily to explain cost and quality coordination, not environmental coordination. When a European retailer adds a chemical restriction to its supplier code, which governance form does that produce? The framework does not say directly, though its logic suggests that the answer depends on how complex and codifiable the environmental requirement is, and on whether the supplier has the capability to meet it.

These limitations matter because the environmental requirements that lead firms now impose on suppliers are, in the Gereffi et al. vocabulary, unusually complex and unusually difficult to codify. A formaldehyde emission standard can be written into a contract and verified by a lab test; that is codifiable. A requirement to demonstrate continuous improvement in energy intensity, or to participate in a carbon accounting exercise that spans the supplier's own upstream chain, is not. It requires judgment, data infrastructure, and a willingness to expose internal processes to external scrutiny. The governance form that such requirements produce is not market, and it is not quite hierarchy. It is something closer to what Ponte and Gibbon (2005) called "quality conventions"—shared understandings of what counts as good practice, enforced through audit and reputation rather than through price or ownership.

2.1.2 Buyer-Driven and Producer-Driven Chains

Before the Gereffi et al. framework, the field organized itself around a simpler dichotomy. Gereffi (1994) distinguished between "buyer-driven" commodity chains, in which large retailers and brand owners coordinate production networks in labor-intensive consumer goods, and "producer-driven" chains, in which manufacturers with proprietary technology coordinate networks in capital-intensive sectors such as automobiles and electronics. The distinction was never absolute—Apple is a producer that behaves like a buyer, Walmart is a buyer that behaves like a producer in its logistics operations—but it captured something real about where power sits in different industries and what kind of upgrading is possible for firms in developing countries.

The buyer-driven model dominated the early literature on Chinese manufacturing because so much of China's export success in the 1990s and 2000s ran through buyer-driven chains: apparel, footwear, toys, furniture, consumer electronics assembly. In these chains, the lead firm is a retailer or brand that owns the design and the customer relationship but not the factories. It sets the terms: price, delivery, quality, and increasingly, environmental and social standards. The supplier's bargaining power is weak because the lead firm can credibly threaten to relocate to another country or another factory within the same country. This is the world that the Beijiao furniture makers inhabited, and it explains why a single buyer's questionnaire could, within two years, redirect orders across a border.

Producer-driven chains tell a different story. When a Chinese firm supplies precision components to a German automaker, the automaker cannot easily switch suppliers because the component is designed into the vehicle platform and requalification takes years. The supplier has more bargaining power, more access to technical information, and more opportunity to learn. Environmental requirements in producer-driven chains tend to be more technical and more deeply embedded in product design—lightweighting, material substitution, recyclability—and the supplier is more likely to be treated as a partner in meeting them rather than as a compliance problem. The distinction between buyer-driven and producer-driven governance predicts different environmental trajectories, because it predicts different distributions of information, capability, and bargaining power.

2.1.3 Lead Firm Dynamics and the Exercise of Power

The governance literature has always been interested in power, but it has sometimes been shy about naming it. The language of "coordination" and "governance" can obscure the fact that lead firms in buyer-driven chains exercise a kind of authority that is not so different from the authority of a manager over an employee, minus the employment contract. They specify what is to be produced, how, and increasingly under what environmental conditions. They audit. They sanction. They reward. The supplier that meets the requirements gets more orders; the supplier that does not gets fewer. This is not a market transaction in any meaningful sense. It is a hierarchy that has been outsourced.

Dallas, Ponte, and Sturgeon (2019) pushed this point further by arguing that power in global value chains operates through multiple mechanisms: direct coercion (the threat of exit), agenda-setting (defining what counts as a problem), and normative framing (persuading suppliers that certain practices are legitimate). The environmental implications are significant. When a lead firm defines carbon intensity as a key performance indicator, it changes what suppliers pay attention to. When a lead firm requires third-party certification of forest products, it creates a market for certification bodies and a barrier to entry for suppliers who cannot afford the audit. Governance, in this view, is constitutive: it shapes the identities and capabilities of the firms it governs, not just their prices.

This constitutive dimension is central to the argument of this book. When a European retailer requires its Chinese furniture suppliers to report on the carbon footprint of each product, it is doing more than adding a reporting requirement. It is introducing a new category of knowledge—product-level carbon accounting—into firms that may never have thought in those terms. Some firms will treat this as a bureaucratic burden and comply minimally. Others will internalize the category, build the data systems to support it, and discover that the same data can be used to reduce energy costs, qualify for green procurement contracts, and differentiate their products in domestic markets. The governance relationship creates the initial pressure; the firm's response determines whether that pressure becomes a capability. The literature on governance tells us where the pressure comes from. It does not tell us what happens next. For that, we need the literature on upgrading.

2.1.4 Governance and the Environment: A Gap in the Literature

The classic governance literature says little about environmental performance. Gereffi et al. (2005) mentioned environmental standards only in passing, as one of several non-price requirements that lead firms might impose. Humphrey and Schmitz (2002), in their influential review of governance and upgrading, treated environmental upgrading as a subset of process upgrading, with no separate theoretical status. This is not a criticism of those authors, whose contributions were enormous. It is an observation about the state of the field. The governance literature was built to explain how goods are made and moved, not how their production affects ecosystems and atmospheres.

The gap has begun to close. A growing body of work examines how environmental standards travel through value chains, how lead firms use sustainability requirements to manage risk and reputation, and how suppliers in developing countries respond. Much of this work is empirical and descriptive. It documents that environmental requirements are proliferating, that they are unevenly enforced, and that they create both opportunities and burdens for suppliers. It has not yet produced a theoretical account of why some suppliers convert these requirements into capabilities while others do not. That is the task the green capability turn sets for itself.

2.2 Industrial Upgrading: Economic and Environmental Dimensions

2.2.1 The Fourfold Classification and Its Limits

The upgrading literature begins with a simple observation: firms in developing countries do not stay in the same activity forever. They move. They move from assembling imported components to manufacturing components themselves. They move from manufacturing to design. They move from design to branding. Humphrey and Schmitz (2002) codified these movements into four categories that have structured the field ever since. Process upgrading means producing more efficiently or with fewer defects. Product upgrading means making better products, or products with more functions. Functional upgrading means taking on new activities in the chain, such as design or marketing. Inter-chain upgrading means applying skills learned in one chain to a different chain altogether.

The classification is useful because it distinguishes between different kinds of movement, which have different implications for firm capabilities and for the distribution of gains. Process upgrading can be achieved through better equipment or tighter supervision; it does not necessarily build design or marketing capability. Product upgrading requires understanding what customers want and how to deliver it; it builds a different set of skills. Functional upgrading is the most demanding because it requires the firm to compete with the lead firm's own activities—to become, in effect, a rival rather than a supplier. Inter-chain upgrading is the most transformative because it allows a firm to escape the specific power relations of a single chain.

For all its utility, the classification has a blind spot. It was built to describe economic upgrading—the capture of more value—and it implicitly assumes that economic upgrading is the goal. Environmental performance enters the picture, if at all, as a constraint or a cost. A firm that installs a scrubber to meet an emissions standard is process upgrading, in the sense that it is changing its production process, but the literature has tended to treat this as compliance rather than upgrading. The distinction matters because compliance is defensive and upgrading is offensive. Compliance is something you do because you have to. Upgrading is something you do because it makes you stronger.

The question this book poses is whether environmental performance can be offensive rather than defensive—whether it can be a form of upgrading in its own right, not just a constraint on economic upgrading. The evidence from the case studies presented in later chapters suggests that the answer is sometimes yes, and that the conditions under which it is yes are identifiable. But before we can specify those conditions, we need to understand what the upgrading literature has already said about the relationship between economic and environmental performance, and where it has fallen short.

2.2.2 Environmental Upgrading as a Distinct Category

De Marchi, Di Maria, and Ponte (2013) propose adding environmental upgrading as a distinct category, defining it as "the process by which economic actors move towards a production system that avoids or reduces the environmental costs of their operations and products." The definition is deliberately broad. It includes process changes that reduce emissions or resource use, product changes that reduce environmental impact over the product's life cycle, and organizational changes that improve environmental management. It does not require that the firm capture more economic value; a firm can upgrade environmentally while earning the same margin, or even a lower one, if the environmental improvement is mandated or if the market does not reward it.

The distinction between environmental upgrading and economic upgrading is analytically useful because the two do not always move together. A firm can upgrade economically without upgrading environmentally—by moving into design, for example, while continuing to source from dirty factories. A firm can upgrade environmentally without upgrading economically—by investing in cleaner technology that raises costs without raising prices. And a firm can do both at once, which is the outcome that the green capability turn is designed to explain. The interesting theoretical question is not whether environmental upgrading exists; it plainly does. The question is when it becomes a source of competitive advantage rather than a drag on competitiveness.

De Marchi et al. (2013) offer a partial answer. Drawing on evidence from Italian and Dutch firms, they argue that environmental upgrading is more likely when the lead firm in the chain demands it, when the supplier has prior experience with environmental management systems, and when the institutional environment in the supplier's home country provides support. These findings describe the conditions under which environmental upgrading happens, not the conditions under which it pays. The distinction is important. A firm can be pushed into environmental upgrading by a powerful buyer and find that the investment pays for itself through lower energy costs. Or it can be pushed into environmental upgrading and find that the investment is a pure cost, borne because the buyer will otherwise leave. The same pressure, different outcomes. The upgrading literature describes the pressure; it does not explain the variation in outcomes.

2.2.3 The Upgrading–Environment Nexus: Evidence and Ambiguity

The empirical literature on the relationship between economic upgrading and environmental performance is ambiguous, and it is worth being honest about that ambiguity. Some studies find that firms that upgrade economically also improve their environmental performance, because the technologies and management practices that support quality upgrading also tend to reduce waste and energy use. Other studies find no relationship, or a negative one, because economic upgrading can involve moving into activities that are more energy-intensive or that generate more hazardous waste. The evidence does not support a general claim that economic upgrading is good for the environment. It supports a more modest claim: the relationship depends on the type of upgrading and the sector in which it occurs.

Process upgrading, for example, often reduces environmental impact as a byproduct. A firm that invests in more efficient machinery to reduce unit costs is also likely to reduce energy consumption per unit. A firm that tightens quality control to reduce defect rates is also likely to reduce material waste. These are what the environmental economics literature calls "win-win" outcomes, and they are real, though they are not universal. The win-win logic breaks down when the cheapest way to reduce costs is also the dirtiest—when, for example, a firm can cut costs by switching to a cheaper fuel with higher emissions, or by externalizing waste treatment to an unregulated contractor.

Product upgrading is more variable. A firm that moves from making low-grade furniture to high-grade furniture may use more expensive and more sustainably sourced materials, which is good. Or it may use more finishes and adhesives, which is bad. A firm that moves from making simple electronics to complex electronics may increase its use of rare earth metals, which has significant environmental costs upstream. The environmental impact of product upgrading depends on the product and on the supply chain that supports it. There is no general rule.

Functional upgrading—moving into design, marketing, or branding—has the most ambiguous relationship of all. On one hand, firms that control design can build environmental considerations into products from the start, which is where the largest environmental gains are often found. On the other hand, firms that move into branding may shift their manufacturing to lower-cost suppliers, who may be less environmentally responsible. The lead firm's own environmental footprint may go down while the chain's footprint goes up. This is the "outsourcing emissions" problem that haunts much of the corporate sustainability literature, and it is a reminder that upgrading is not a reliable environmental strategy at the level of the chain, even if it is at the level of the firm.

2.2.4 Why the Upgrading Literature Underestimates Environmental Capability

The upgrading literature has tended to treat environmental performance as a constraint rather than a capability. There are historical reasons for this. The literature emerged in the 1990s, when environmental regulation in developing countries was weak and environmental requirements from lead firms were limited to a few high-profile sectors. The dominant question was how firms in poor countries could escape the low-value trap of assembly work. Environmental performance seemed like a rich-country concern, or a niche market for ethical consumers, not a mainstream determinant of competitiveness.

That framing is now outdated, and the evidence presented in this book suggests that it was always partly wrong. Environmental requirements have become mainstream in many global value chains, not because consumers demand them but because governments regulate them, because investors price them, and because lead firms use them to manage supply chain risk. A Chinese furniture factory that cannot document the formaldehyde emissions of its panel board cannot sell to a European retailer, regardless of its price. A Chinese electronics assembler that cannot report the carbon footprint of its operations cannot qualify as a supplier to a company with a science-based emissions target. These are not niche requirements. They are conditions of participation.

Once environmental performance gates participation, it functions as a capability. A firm that can meet the condition has access to the chain; a firm that cannot is excluded. The capability to meet environmental requirements is not the same as the capability to produce at low cost, and it is not automatically acquired by firms that are good at cost reduction. It requires different skills: the ability to measure emissions and resource use across supply chain partners, and the ability to interpret and anticipate regulatory requirements. These skills are what I mean by green governance capability, and they are the missing variable in the upgrading literature's account of who moves up and who stays put.

2.3 The Green Capability Turn: Integrating Institutional and Resource-Based Views

2.3.1 Why a New Framework Is Needed

The governance literature tells us where environmental pressure comes from. The upgrading literature tells us what firms do in response. Neither tells us why firms respond differently to the same pressure, or why some responses produce durable competitive advantage while others produce only temporary compliance. To answer those questions, we need a framework that connects the external institutional environment to the internal capabilities of the firm. The green capability turn is that framework. It draws on two bodies of theory that are often treated as rivals—institutional theory and the resource-based view—and argues that they are complementary when applied to the problem of environmental governance in global value chains.

Institutional theory explains why firms adopt practices that are not obviously profitable. Firms conform to institutional pressures—regulatory requirements, norms, and expectations from stakeholders—because conformity confers legitimacy, and legitimacy is a condition of survival. The theory has been applied extensively to environmental management, where it explains why firms adopt ISO 14001 certification, why they publish sustainability reports, and why they join voluntary programs even when the direct economic benefits are unclear. The weakness of institutional theory is that it predicts convergence: if all firms face the same institutional pressures, they should all adopt the same practices. In practice, they do not. Some firms adopt deeply; others adopt superficially. Some build capabilities; others buy certificates.

The resource-based view explains why firms differ. Firms are bundles of resources and capabilities that are heterogeneously distributed and imperfectly mobile. A capability that is valuable, rare, difficult to imitate, and non-substitutable can be a source of sustained competitive advantage. The theory has been applied to environmental management through the "natural resource-based view" of Hart (1995), which argued that environmental constraints can drive the development of new capabilities—pollution prevention, product stewardship, sustainable development—that are sources of competitive advantage. The weakness of the resource-based view is that it is often tautological: a capability is defined as something that produces advantage, and advantage is explained by the presence of the capability. It also has little to say about where capabilities come from, or why firms in the same industry and country develop different ones.

The green capability turn combines the two. Institutional pressures, especially those transmitted through global value chain governance, create the initial impetus for firms to invest in environmental management. But the outcome of that investment—whether it produces a capability or just a cost—depends on how the firm integrates the new practices with its existing resources and routines. Firms that treat environmental requirements as an opportunity to rethink their production processes, their data systems, and their product designs are more likely to build capabilities than firms that treat them as a compliance exercise to be minimized. The institutional environment sets the stage; the firm's internal response determines the plot.

2.3.2 Institutional Pressures Along the Value Chain

The institutional pressures that drive environmental upgrading in Chinese manufacturing come from three sources, and they operate through different mechanisms. The first is regulation. China's environmental laws, and especially the dual carbon goals announced in 2020, create legal requirements and policy signals that firms must respond to. The regulatory pressure is strongest in sectors that are directly covered by emissions trading or energy intensity targets, and weaker in sectors that are not. But even firms in uncovered sectors face pressure through local government implementation, through supply chain requirements that reference regulatory standards, and through the expectation that regulation will tighten over time.

The second source is the global value chain. Lead firms impose environmental requirements on their suppliers through codes of conduct, supplier scorecards, audit programs, and procurement specifications. These requirements are often stricter than local regulation, and they are enforced through the threat of losing orders rather than through legal sanction. The governance literature has documented the proliferation of these requirements, and the case studies in this book show how they operate in practice. A furniture factory in Shunde that supplies a European retailer must meet the retailer's chemical restrictions, which are based on EU regulations but applied to production in China. The factory is, in effect, subject to European law through a commercial relationship.

The third source is the capital market. Investors, lenders, and insurers are increasingly pricing environmental risk, and Chinese manufacturers that export to regulated markets are exposed to that pricing. A factory that cannot demonstrate compliance with environmental standards may find it harder to obtain financing, or may pay a higher interest rate. The pressure is indirect, but it is real, and it is growing. The three sources interact: a regulatory tightening in China can trigger a value chain requirement from a foreign buyer, which in turn affects the firm's access to capital. The institutional environment is not a single pressure but a system of pressures, and firms that can read the system are better positioned to respond strategically.

2.3.3 Absorptive Capacity and the Conversion of Pressure into Capability

The central mechanism in the green capability turn is absorptive capacity—the ability of a firm to recognize the value of new information, assimilate it, and apply it to commercial ends. Cohen and Levinthal (1990) developed the concept to explain why some firms benefit more from external knowledge than others. The logic is straightforward. An environmental requirement is a piece of information. It specifies a standard, a measurement method, or a management practice that the firm did not previously use. Whether the firm benefits from this information depends on whether it has the prior knowledge and the organizational routines to absorb it.

Absorptive capacity is not the same as size, though the two are correlated. A large firm can afford to hire environmental engineers and buy monitoring equipment, which raises its absorptive capacity. But a small firm with a technically sophisticated owner and a culture of continuous improvement can have high absorptive capacity relative to its size. The case studies in later chapters include both large firms that failed to absorb environmental requirements and small firms that absorbed them quickly. The difference is not resources alone. It is the presence of what Cohen and Levinthal called "prior related knowledge"—an understanding of the production process that allows the firm to see how an environmental requirement connects to what it already does.

Absorptive capacity also depends on the firm's relationships with external actors. A firm that participates in industry associations, collaborates with universities, and maintains close ties with its suppliers has more channels through which new information can enter and be interpreted. The cluster literature, which I reviewed in my earlier work on the internationalization of industrial clusters, is relevant here. Firms in clusters have access to a dense network of local relationships that can support learning, provided the cluster has institutions that facilitate knowledge sharing. The same cluster can be a source of capability or a source of inertia, depending on whether its institutions are oriented toward upgrading or toward protecting existing practices.

2.3.4 The Role of Organizational Slack and Managerial Attention

Two internal conditions moderate the conversion of institutional pressure into capability: organizational slack and managerial attention. Organizational slack is the cushion of resources that allows a firm to experiment, to absorb failures, and to invest in activities that do not pay off immediately. Firms with slack are more likely to treat an environmental requirement as an opportunity to learn; firms without slack are more likely to treat it as a threat to be minimized. This is one reason why environmental upgrading is often easier for firms that are already profitable, and why it is harder for firms that are struggling. The relationship is not deterministic—some firms with slack waste it, and some firms without slack are forced to innovate—but it is a strong tendency.

Managerial attention is the allocation of cognitive resources to a particular issue. Environmental requirements compete for attention with cost, quality, delivery, and a hundred other concerns. Firms whose managers see environmental performance as central to the business are more likely to invest in the capabilities needed to meet it. Firms whose managers see it as a distraction are more likely to comply minimally and move on. The difference is not just a matter of attitude. It reflects the manager's understanding of the business environment—whether environmental performance is a source of risk or a source of advantage, whether the firm's customers value it, and whether the regulatory trajectory is toward tighter or looser standards. Managers who read the environment correctly are more likely to allocate attention in ways that build capability.

2.3.5 From Compliance to Capability: A Typology of Firm Responses

Combining the institutional and resource-based perspectives yields a typology of firm responses to environmental pressure. The typology is not a set of boxes into which firms can be sorted permanently. Firms move between categories as their capabilities and their institutional environments change. But the categories are useful for organizing the evidence and for identifying the conditions under which pressure becomes capability.

Some firms resist. They deny the legitimacy of the requirement, dispute the evidence, or seek to avoid enforcement. Resistance is most common when the requirement is new, when enforcement is weak, and when the firm has little slack. It is a rational response for a firm that expects the requirement to go away, but it is a losing strategy when the requirement is backed by a powerful buyer or a determined regulator. Firms that persist in resistance eventually face exclusion from the chain or legal sanction.

Most firms comply. They meet the letter of the requirement but do not internalize it. They buy the certificate, install the equipment, and file the report, but they do not change their routines or build new capabilities. Compliance is the modal response in many industries, and it is not irrational. It minimizes cost and satisfies the immediate demand. But it leaves the firm vulnerable to the next tightening of the requirement, because it has not built the capacity to anticipate or adapt. Compliance is a treadmill: the firm runs to stay in place.

A smaller group practices what I call strategic compliance. The firm meets the requirement and uses the process of meeting it to build capabilities that have value beyond the specific requirement. It develops a data system for tracking emissions that can also be used for energy management. It trains staff in environmental management who can later take on broader operational roles. It redesigns a product to meet a chemical restriction and discovers that the redesign also reduces material costs. Strategic compliance is the entry point to the green capability turn. The firm is still responding to external pressure, but it is capturing some of the value of its response.

A few firms build capability. They treat environmental performance as a source of competitive advantage and invest in the capabilities needed to lead rather than follow. They anticipate regulatory changes, develop proprietary processes, and position themselves as partners to buyers who are trying to meet their own environmental targets. Capability building is the outcome that the green capability turn is designed to explain. It is not common. Most firms in most industries do not reach this stage. But it is real, and the case studies in this book show how it happens.

2.3.6 The Green Governance Capability Construct

The central construct of the framework is green governance capability. I define it as the organizational capacity to measure, manage, and improve environmental performance in ways that meet external requirements and create competitive advantage. The definition has three parts, and each corresponds to a distinct set of activities.

Measurement is the foundation. A firm cannot manage what it cannot measure, and it cannot demonstrate compliance without credible data. Measurement capability includes the ability to conduct carbon accounting, to monitor emissions and resource use, to track the environmental attributes of inputs, and to verify the accuracy of the data. It also includes the ability to interpret measurement standards—the GHG Protocol, ISO 14064, product category rules—and to apply them correctly. Measurement is not glamorous, but it is where most firms fail. The Beijiao furniture makers who could not answer the forty-page questionnaire failed at measurement before they failed at anything else.

Management is the second component. Measurement without management is just reporting. Management capability includes the ability to set targets, allocate responsibility, integrate environmental considerations into operational decisions, and monitor progress. It also includes the ability to work with suppliers and customers to improve environmental performance across the chain. A firm that can measure its own emissions but cannot influence its suppliers' emissions has limited green governance capability, because a large share of the environmental impact of manufactured products occurs upstream.

Improvement is the third component. Management without improvement is just administration. Improvement capability includes the ability to redesign products and processes to reduce environmental impact, to adopt new technologies, and to learn from experience. It is the component that is most closely linked to innovation, and it is the component that is most likely to produce competitive advantage. A firm that can continuously improve its environmental performance is a moving target for regulators and competitors alike.

The three components are sequential in logic but not in practice. A firm can start with improvement—adopting a cleaner technology because it is cheaper—and then build measurement and management around it. A firm can start with measurement—responding to a buyer's data request—and then discover that the data reveals opportunities for improvement. The sequence matters less than the integration. Firms that build all three components and connect them to their core business strategy are the ones that turn environmental pressure into competitive advantage.

2.3.7 Scope Conditions and Boundary Cases

The green capability turn is not a universal theory. It applies under specific conditions, and it is important to be clear about what those conditions are. The first condition is that environmental requirements are credible and enforced. If a buyer imposes a requirement but does not enforce it, or if a regulator sets a standard but does not inspect, firms have no incentive to invest in capability. The framework assumes that at least some external actor is monitoring performance and imposing consequences. The evidence in later chapters suggests that enforcement is uneven, and that the framework applies most clearly in segments of the value chain where enforcement is strong.

The second condition is that the firm has some degree of strategic choice. A firm that is wholly dependent on a single buyer, with no alternative customers and no slack, may have no option but to comply minimally. A firm that has multiple customers, or that sells in domestic markets as well as export markets, has more room to invest in capability. The framework does not assume that all firms can choose their response, but it does assume that some can, and it explains why they choose differently.

The third condition is that the environmental requirement is technically tractable. Some environmental problems are easy to measure and solve; others are not. A requirement to reduce packaging waste is tractable. A requirement to eliminate all hazardous chemicals from a complex product is harder. The framework is more likely to apply when the requirement can be broken down into manageable steps, and when the firm can see a path from its current practice to the required practice.

The boundary cases are as important as the core cases. Firms that resist environmental requirements despite strong enforcement are a boundary case that the framework does not fully explain. Firms that build green capabilities for reasons unrelated to external pressure—because the founder is an environmentalist, because the firm wants to attract talent—are another. The framework is designed to explain the conversion of external pressure into internal capability, not the origins of all environmental behavior. It is a partial theory, and it should be judged as such.

2.3.8 Linking the Framework to the Empirical Chapters

The chapters that follow apply the framework to three groups of industries, distinguished by factor intensity. Chapter 5 examines labor-intensive industries, where environmental pressure interacts with cost pressure and where relocation is a live option. Chapter 6 examines technology-intensive industries, where eco-innovation is a source of competitive advantage and where the race for green technological capability is most visible. Chapter 7 examines capital-intensive industries, where process substitution is expensive and where stranded assets are a real risk. Each chapter asks the same questions: What institutional pressures are firms facing? How are they responding? What determines whether the response produces capability or just compliance? The answers vary by sector, but the framework provides a common language for comparing them.

The furniture case in Chapter 9 is a particularly important test. Furniture is a traditional labor-intensive industry, and it is often assumed that such industries cannot upgrade environmentally because they compete on cost. The case shows that this assumption is too simple. Some furniture firms in China have built green governance capabilities that allow them to meet the most demanding European standards, and they have used those capabilities to maintain market access and to move into higher-value segments. Other firms have not, and they have relocated or exited. The difference is not explained by factor intensity alone. It is explained by the presence or absence of the capabilities that the green capability turn identifies.

2.3.9 Measurement, Verification, and the Limits of the Framework

One limitation of the framework deserves emphasis. Green governance capability depends on measurement, and measurement depends on data. The data available to firms, regulators, and researchers is often incomplete, inconsistent, and unverified. Chapter 3 examines the measurement infrastructure—carbon accounting standards, MRV systems, and the boundaries of evidence—in detail. For now, it is enough to note that the framework's predictions are conditional on data quality. A firm that cannot measure its emissions cannot manage them, and a researcher who cannot verify a firm's claims cannot assess its capability. The green capability turn is a theory about what firms can do with good data. It is not a theory about what firms can do without it.

This is not a fatal limitation. It is a scope condition, and it is one that the book addresses directly. The measurement infrastructure is improving, and the firms that invest in it are building a capability that will be more valuable as the infrastructure matures. The framework is designed to explain the early movers, not the laggards. The laggards may catch up as measurement becomes cheaper and more standardized, or they may exit. Either way, the framework's logic holds: the firms that can measure, manage, and improve are the ones that will thrive in a carbon-constrained world.

2.3.10 Conclusion: A Framework, Not a Verdict

The theoretical foundations laid out in this chapter are not a conclusion. They are a set of tools for organizing evidence and for asking better questions. The governance literature tells us that power in global value chains is concentrated in lead firms, and that the exercise of that power shapes the capabilities of suppliers. The upgrading literature tells us that firms can move from low-value to high-value activities, but that the movement is not automatic and that environmental performance has been treated as a constraint rather than a capability. The green capability turn integrates these insights with institutional theory and the resource-based view to explain why some firms convert environmental pressure into competitive advantage while others do not.

The framework's central claim is that green governance capability is an endogenous driver of industrial upgrading, not a passive product of regulatory compliance. This claim is testable, and the chapters that follow test it against evidence from Chinese manufacturing. The evidence will not be uniform. Some firms will fit the framework; others will not. Some industries will show clear patterns; others will show messy variation. The value of the framework is not that it predicts every outcome, but that it identifies the mechanisms that produce the outcomes we observe. Those mechanisms—absorptive capacity, organizational slack, managerial attention, and the integration of measurement, management, and improvement—are the subject of the rest of the book.

The Beijiao furniture makers who could not answer the buyer's questionnaire are not a morality tale. They are a data point. Some of their neighbors adapted, and some did not. The ones who adapted did not necessarily have more resources or better technology. They had the capacity to learn from a requirement that others treated as a nuisance. That capacity is what this book is about, and the theoretical framework developed in this chapter is an attempt to explain where it comes from and why it matters.