The Climate-Policy Chain, Made Simple

1. SDGs, carbon management and the problem this lesson solves

In practice, begin with a premise you can carry into your own workplace: climate goals rarely reach a factory as abstract ideals. They arrive as questionnaires, verification appointments, allowance prices and — if you export into the European Union — as carbon costs embedded in trade. The United Nations Sustainable Development Goals, especially SDG 13 (Climate Action), together with SDG 7 (affordable clean energy), SDG 9 (industry and innovation) and SDG 12 (responsible production), give you a shared language for why that pressure exists. They do not, by themselves, tell you which meter to install or which subcontracted finishing step could weaken a CBAM file.

Carbon management is the organisational craft that sits between goals and instruments. You work through it as a cycle: define what counts; measure activity and emissions; reduce where it matters; report in a form others can trust; and finance the transition without mistaking a brochure for a pathway. When that craft is weak, policy can feel arbitrary and punitive. When it is strong, you can turn the same policy into a constraint your plant can navigate.

Accordingly, this lesson has a more practical purpose than simply asking you to “learn sustainability.” It helps you reconstruct the climate-policy chain that connects global goals to Turkish law and markets, and from there to the factory gate — so that you can argue, cite and sequence action while testing common assumptions carefully (see Figure 1).

2. From global goals to climate policy instruments

From 2015 onward, the Paris Agreement locked in a logic of nationally determined pathways (NDCs). The genius — and the frustration — of Paris is that it is polycentric: countries choose their contributions, then must invent domestic instruments capable of delivering them. Carbon pricing (taxes or emissions trading), performance standards, industrial policy, fossil-fuel subsidy reform and public procurement all become candidates. Baranzini et al. (2017) argue that carbon pricing is powerful because it is incomplete: it works best alongside technology and innovation policy, not as a lonely purity test. You should watch the short UN explainer video below before you continue.

However, critical scrutiny still matters. Green’s (2021) ex-post review of carbon-pricing evaluations is uncomfortable reading for slogan-makers: surprisingly few studies rigorously measure emissions reductions (37 in her set, mostly Europe), and results depend heavily on design — caps, allocation, enforcement, complementary measures. Aggregate reductions attributed to pricing are often about 0–2% per year; EU ETS studies in her synthesis cluster around 0–1.5% per year. “We have a carbon price” is not the same claim as “our carbon price is cutting emissions.” Learning to hold that distinction is one of the most useful professional habits this course can give you.

Narassimhan et al. (2018) turn the same lesson into a practice checklist across eight jurisdictions: environmental effectiveness, economic efficiency, market management, revenue management and stakeholder engagement.

Meanwhile, the EU’s deepening of its ETS and the European Green Deal (from 2019) raised a second-order problem: if one jurisdiction prices carbon hard while others do not, carbon leakage and competitiveness disputes intensify. That is the doorway through which border carbon adjustments walk into the story (see Table 1).

3. Why borders entered the story: BCAs and CBAM

Keen, Parry and Roaf (2022) summarise the economic rationale of border carbon adjustments (BCAs): when carbon-price disparities are large, a well-designed BCA is among the more coherent domestic tools for addressing leakage and competitiveness — though design details (sector coverage, benchmarks, treatment of exports, recognition of foreign pricing) decide whether the tool is workable diplomacy or a trade fight waiting to happen. Zhong and Pei (2024), reviewing 97 economic studies with a PRISMA protocol, underline the same core logic: level the playing field and reduce leakage through carbon-content-based border measures — which is why embedded-emissions accounting, not slogans, sits at the centre of the instrument. Their synthesis also warns that there is no one-size-fits-all CBAM design: coverage of trade and sectors, treatment of carbon content, and use of revenues change effectiveness across fair competition, leakage and welfare objectives.

In line with this logic, the EU’s Carbon Border Adjustment Mechanism (CBAM) is currently the most advanced import carbon-cost mechanism in operation (CITD, 2024). It begins with energy-intensive, trade-exposed goods — iron and steel, aluminium, cement, fertilisers, electricity and hydrogen — precisely because those sectors sit at the intersection of climate ambition and trade politics. The European Parliament Research Service explainer video below walks through how CBAM works at the border; the Commission hub that follows is a useful official landing page for the same instrument.

Smith, Overland and Szulecki (2023) remind us that CBAM is also foreign policy: which “significant others” the EU engages (major emitters, vulnerable exporters, political allies) shapes whether the instrument succeeds or hardens into conflict. IEEP (2025) adds the equity lens: low- and middle-income suppliers face feasibility and fairness stress, even as 2025 simplification debates try to reduce administrative burden.

By contrast, comparative modelling sharpens the caution for exporters. Bellora and Fontagné (2023) show that CBAM can reduce leakage while still raising the EU ETS price and leaving uncovered downstream and export channels exposed. Perdana and Vielle (2022) find leakage reductions on the order of one-third by 2040 under their scenarios, with LDC exemptions able to worsen leakage and revenue recycling into clean energy performing better. None of those results imply that a domestic ETS elsewhere deletes product-data asks. Erdogdu (2025) maps the opportunity–challenge pair for non-EU countries specifically: alignment and innovation pressure on one side; administrative burden and trade friction on the other — including tension with Paris “common but differentiated responsibilities” when a uniform carbon-content price is applied at the border. Reeve and Aisbett (2022) add the accounting foundation: consistent public emissions-accounting systems are a prerequisite if border instruments, linked markets and certification schemes are to be effective and WTO-facing.

4. Mapping the climate-policy chain

Against this backdrop, the workable map for this course has five links:

1. Paris / NDC — the political pathway
2. CCMSAP 2024–2030 — the national sector strategy
3. Climate Law 7552 — the legal hinge
4. MRV and TR ETS — measurement and the domestic carbon price
5. CBAM and buyer questionnaires — border and contract pressure

If you miss one link, the story can slide into a misleading shortcut: that a Turkish ETS will erase CBAM; that MRV is only paperwork; or that SDGs alone are enough. You should keep all five in view. So, we can say that you can brief your board with clarity and confidence (see Figure 2).

5. Türkiye’s strategic frame: NDC, CCMSAP and 2053

Meanwhile, Türkiye’s long-term narrative includes a 2053 net-zero aspiration. An aspiration without instruments remains only a political statement. The Climate Change Mitigation Strategy and Action Plan (CCMSAP) 2024–2030 is one of the main bridges from that statement to practice: it organises sector pathways for energy, industry, buildings and related domains under the Paris/NDC frame. For manufacturers, CCMSAP functions as a radar of where public programmes, reporting expectations and investment narratives are likely to concentrate through 2030.

Accordingly, for your strategy team, a workable habit is simple. Maintain a one-page matrix with CCMSAP/NDC milestones on one axis and your products and EU exposure on the other. That matrix helps you recognise each buyer request as part of a predictable policy cascade rather than an unexpected crisis (see Table 2).

So, we should read CCMSAP as a radar, not as a plant SOP (standard operating procedure). It tells you where public programmes, reporting expectations and investment narratives are likely to concentrate. It does not replace installation monitoring plans, product-intensity worksheets or buyer-specific templates. If you treat a strategy document as if it were a meter, you may overclaim; if you ignore it, you may be surprised by the direction of policy.

6. Climate Law 7552 — the domestic legal hinge

Climate Law No. 7552, published in the Official Gazette on 9 July 2025, is the hinge of the Turkish chain. It establishes the legal and institutional frame for greenhouse-gas mitigation and climate adaptation — including planning tools, climate-related revenues, permits and supervision. Critically for this course, it authorises a national ETS, sets expectations around carbon credits / offsetting, and situates Türkiye’s approach in relation to EU CBAM.

In practice, day-to-day climate administration sits with the Directorate of Climate Change. Market and registry functions are associated with Energy Exchange Istanbul (EXIST / EPİAŞ). A Carbon Market Board provides governance oversight. Professional bulletins emphasise that the Law hardens enforcement: late or missing verified emission reports can attract substantial administrative fines (KPMG Vergi, 2025; Kabine Law, 2025). Local government relays, such as İstanbul’s municipal climate pages announcing the Law, show how quickly the message travels from Official Gazette to municipal and industrial ecosystems.

That said, Hondur’s (2025) assessment of Türkiye’s ETS draft regulation makes a point that managers need: environmental effectiveness depends on the quality of the cap, the allocation method, market-stability design, MRV capacity and fiscal integrity against abuse — not on the mere existence of a law titled “climate.” CBAM pressure, Hondur notes, is one reason ETS design cannot be treated as a slow academic exercise.

7. MRV since 2015 — the market sits on measurement

Meanwhile, Türkiye did not invent monitoring when it wrote Climate Law. The Regulation on Monitoring of Greenhouse Gas Emissions created an MRV architecture that has operated since the mid-2010s for Annex-1 style activities. Covered operators prepare an approved monitoring plan, monitor accordingly, obtain verification from accredited verifiers, and submit annual emission reports (classically by 30 April). Approximately 800 installations have been covered, representing on the order of half of national GHG emissions.

Accordingly, the Climate Change Directorate’s 2025 verification work assignment via MEDAS (Central Electronic Verifier Assignment System) for hundreds of facilities underscores that verified reports are treated as the data backbone for national ETS preparations. The arithmetic is deliberately boring — activity data × emission factor — and deliberately powerful when it is verified, timestamped and comparable across years.

8. Building a Turkish ETS under CBAM pressure

You should treat this section as a design conversation, not a shopping list. It is where domestic market design meets border pressure — and where comparative evidence should make you appropriately cautious.

An ETS caps emissions allowances and allows trade so that abatement occurs where marginal costs are lowest. Narassimhan et al. (2018), reviewing systems including the EU ETS, California, Québec, RGGI, New Zealand, Korea and Chinese pilots, argue that successful carbon markets depend on institutional learning, administrative prudence, revenue management and stakeholder engagement. Caps that tighten on a published schedule, transparent registries, and revenue recycling into transition support are not optional decorations; they are how markets survive political stress. Green (2021) supplies the ex-post caution that sits beside that checklist: average annual reductions under many pricing schemes remain limited unless design and complementary policy are serious. You should watch the EU ETS explainer video below, then skim the draft TR ETS materials that follow for how Türkiye is translating the same market logic.

Türkiye’s pathway draws on earlier Partnership for Market Readiness (PMR) materials and on the Türkiye ETS Regulation governing MRV-linked market rules. A pilot phase has been widely expected from 2026 as the system moves from readiness into operation under Climate Law. Exact thresholds and obligation lists will continue to evolve — which is precisely why scenario literacy beats rumour literacy.

Nevertheless, firm-level evidence deserves a closer look. Chen, Zhang and Chen (2021), studying China’s ETS pilots, find that the “weak” Porter hypothesis was not realised in their sample: the share of green patents fell by about 9.26%, with stronger inhibition among small-scale, manufacturing and non-state-owned firms. Many companies met targets by cutting output and R&D cash flow rather than by innovating. If you advise a mid-sized manufacturer, you should pause over that result. It does not mean “never price carbon.” It means: design and firm capabilities decide whether pricing induces innovation or attrition — the same accuracy habit Lesson 2 will formalise as a four-question claim test.

In line with this, official Turkish communications (Climate Change Directorate ETS–CBAM presentation, 23 February 2024) state the linkage clearly: a credible domestic ETS and verified monitoring strengthen exporters; they do not automatically remove CBAM obligations for EU importers. Bellora and Fontagné (2023) and Perdana and Vielle (2022) make the same structural point from the modelling side: leakage can fall without product-data obligations disappearing. That is the hinge connecting Section 8 to Section 9.

9. CBAM in practice: chronology, politics and Turkish exporters

Implementation timeline

The EU’s Fit for 55 package and the CBAM Regulation (2023) established the legal basis for the mechanism. A transitional reporting phase ran from 1 October 2023 to the end of 2025. From 2026, the definitive regime begins to phase in certificate obligations for EU importers. Policy debates in 2025 about administrative simplification (IEEP, 2025; Ministry of Trade updates) matter for smaller trade flows, but they do not remove the underlying requirement for credible product and installation data.

In practice, for Turkish exporters, CBAM often arrives first as a buyer questionnaire, not as a fine from Brussels. Default values and estimates exist in the EU methodology, yet buyers and intermediaries increasingly prefer measured data because defaults can raise commercial costs (CITD, 2024). Anadolu Agency reporting (2025) quoting Ankara Chamber of Industry leadership is direct: firms unable to provide verifiable emission data risk serious EU market losses. Chamber guides such as ASO’s CBAM firm guide translate that warning into checklists. You should treat them as grey literature with operational value, then verify claims against Ministry of Trade guidance and primary EU texts before signing a supplier declaration.

The Turkish press and ministry pages below show how SKDM and data readiness are already discussed as export competitiveness issues — not distant Brussels theory. The forum video that follows adds a practitioner walk-through of the same border instrument.

That said, Smith et al. (2023) and IEEP (2025) also situate CBAM in political context: it is a contested externalisation of EU climate policy, not a neutral accounting spreadsheet. Russia’s WTO complaint (noted in IEEP’s 2025 brief) is a reminder that border carbon measures live in diplomacy as much as in customs forms. For a Turkish manufacturer, the practical implication is straightforward: a credible data trail is part of trade readiness.

10. What the chain implies for sequencing (now → later)

If Sections 1–9 felt like moving parts, this section is the consequence, not a sudden checklist from nowhere.

You now know that SDGs and Paris set direction; CCMSAP organises national sector pathways; Climate Law authorises markets and enforcement; MRV supplies verified numbers; ETS prices domestic carbon (with design risks that can hurt small firms if support is weak); CBAM prices embedded carbon at the EU border and hits exporters through buyers long before anyone “feels ready.” Zhao et al. (2024) — the empirical case that follows — show that border pressure alone can punish exporters commercially while delivering limited industry-wide carbon cuts unless domestic abatement policy is serious. Chen et al. (2021) show that poorly supported firms may shrink rather than innovate under ETS pilots.

Accordingly, sequencing is not a slogan. For you, it is risk management under uncertainty:

Near term (this quarter / this year) grows out of CBAM buyer clocks + MRV enforcement under Climate Law: you should map whether your products (or your customers’ products) sit in CBAM-exposed sectors; organise installation- and product-level activity data; replace opaque “plant averages” with traceable product data; track Climate Change Directorate / ETS calendars if you are or may become covered; answer buyer questionnaires with documented methods; and put data clauses into subcontractor purchase orders before the next EU reporting cycle.

Medium term (1–3 years), meanwhile, grows out of ETS design evolution + abatement economics: full ETS compliance if obligated; deeper fuel-switch and process capex guided by hotspot maps; green-finance cases that rest on verified pathways; board scenarios that price both domestic carbon costs and border exposure.

A concise board-level statement of the same logic is: this is not sustainability theatre; it is aligning measurement, domestic pricing readiness and export-data credibility because the policy chain has already reached the factory gate.

References

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Ankara Chamber of Industry. (n.d.). CBAM firm guide. https://www.aso.org.tr/

Baranzini, A., van den Bergh, J. C. J. M., Carattini, S., Howarth, R. B., Padilla, E., & Roca, J. (2017). Carbon pricing in climate policy: Seven reasons, complementary instruments, and political economy considerations. WIREs Climate Change.

Chen, Z., Zhang, X., & Chen, F. (2021). Do carbon emission trading schemes stimulate green innovation in enterprises? Evidence from China. Technological Forecasting & Social Change, 168, 120744.

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Green, J. F. (2021). Does carbon pricing reduce emissions? A review of ex-post analyses. Environmental Research Letters, 16, 043004.

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Istanbul metropolitan climate pages. (2025). Climate Law announcement. https://cevre.ibb.istanbul/iklim-degisikligi-sube-mudurlugu/iklim-kanunu-yayimlandi/

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KPMG Vergi. (2025, 9 July). Climate Law of 9 July 2025 [Bulletin]. https://kpmgvergi.com/yayinlar/mali-bultenler/gumruk/09072025-tarihli-iklim-kanunu/3151

Narassimhan, E., Gallagher, K. S., Koester, S., & Rivera Alejo, J. (2018). Carbon pricing in practice: A review of existing emissions trading systems. Climate Policy, 18(8).

Republic of Türkiye. (2024). Climate Change Mitigation Strategy and Action Plan 2024–2030 (EN). https://iklim.gov.tr/db/turkce/icerikler/files/CLIMATE%20CHANGE%20MITIGATION%20STRATEGY%20AND%20ACTION%20PLAN%20_EN%281%29.pdf

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Smith, I. D., Overland, I., & Szulecki, K. (2023). The EU’s CBAM and its ‘significant others’: Three perspectives on the political fallout from Europe’s unilateral climate policy initiative. Journal of Common Market Studies.

Ministry of Trade (Türkiye). (n.d./2026 updates). EU Carbon Border Adjustment Mechanism. https://ticaret.gov.tr/

United Nations. (2015). Transforming our world: The 2030 Agenda for Sustainable Development (SDGs).

Zhao, L.-T., Chen, Z.-Y., Duan, Y.-X., & Qiu, R.-X. (2024). How will CBAM affect the decarbonisation of steel industry in China? A system dynamics approach. International Journal of Production Research, 62(18), 6859–6880. https://doi.org/10.1080/00207543.2023.2285397

Zhong, J., & Pei, J. (2024). Carbon border adjustment mechanism: a systematic literature review of the latest developments. Climate Policy, 24(2), 228–242.

Erdogdu, E. (2025). The Carbon Border Adjustment Mechanism: opportunities and challenges for non-EU countries. WIREs Energy and Environment.

Reeve, A., & Aisbett, E. (2022). National accounting systems as a foundation for embedded emissions accounting in trade-related climate policies. Journal of Cleaner Production, 371, 133678.