Where does industrial decarbonisation in Morocco start?
Industrial decarbonisation in Morocco starts with knowing where each plant’s emissions come from: combustion, process reactions or purchased electricity. That split, which is specific to each sector, decides which levers to study and in what order.
The overall plan (target, pathway, governance, financing, prioritisation method) is covered on our decarbonisation strategy page. This guide goes one level down: what changes when the plant is a cement works, a fertiliser complex, a steel mill, a food factory, a textile mill or an automotive supplier.
Three families of emissions to separate from day one:
- Combustion emissions: kilns, boilers, dryers, generators, company vehicles and plant (scope 1).
- Process emissions: those released by a chemical reaction, whatever the energy used. Calcining limestone into clinker releases CO2; making nitric acid releases nitrous oxide (N2O). They are scope 1 too, but no fuel switch removes them.
- Emissions from purchased electricity and steam (scope 2), plus scope 3: purchased materials, transport, use and end of life of products.
The baseline is a greenhouse gas inventory under ISO 14064-1:2018 — Greenhouse gases — Part 1: Specification with guidance at the organization level for quantification and reporting of greenhouse gas emissions and removals, or under the GHG Protocol Corporate Standard (revised edition, 2004) and its Corporate Value Chain (Scope 3) Standard of 2011. Both are under revision: draft ISO/WD 14064-1.2 at stage 20.60 on iso.org on 11 November 2026, and a consolidated GHG Protocol–ISO standard in preparation. The current editions remain the reference. Our ISO 14064-1 guide details the method, and the carbon footprint ISO 14064 page describes our support.
This article deliberately gives no emission figures by sector and no average gain per lever: they vary from one plant to the next, and a credible plan contains only figures traceable to your meters, analyses and invoices.
Which decarbonisation levers apply in each industrial sector?
Each sector has two or three dominant sources, and the levers follow them. The table sums up the main sources, the levers to study first and the data most often missing.
Sector | Main sources | Levers to study | Data often missing |
|---|---|---|---|
Cement | Limestone calcination (process), kiln fuels, mill electricity | Clinker ratio, alternative fuels, kiln thermal efficiency, waste heat recovery, renewable electricity | Raw meal and clinker composition, calorific value and carbon content of fuels by batch |
Fertilisers | Drying and granulation, steam and electricity of acid plants, N2O from nitric acid if produced, purchased ammonia | Better use of sulphuric acid heat, dryer efficiency, catalytic N2O abatement, ammonia supplier data | Site steam balance, emissions by product line, emissions data for purchased precursors |
Steel | Electric arc furnace or rolling-mill reheating furnace, electricity, oxygen and electrodes | Furnace and mill efficiency, reheating furnace fuel, renewable electricity, scrap quality | Electricity per heat, scrap and input material balance |
Food and beverage | Steam (boilers), industrial refrigeration, refrigerants, packaging, logistics | Heat recovery, refrigeration efficiency, refrigerant tightness and substitution, solar heat, packaging | Refrigerant inventory and top-ups, sub-metering of refrigeration and steam |
Textiles | Finishing heat (dyeing, drying, stenters), spinning and weaving electricity, purchased fibres | Heat recovery on dye baths and stenters, boiler efficiency, variable-speed drives, fibres and suppliers | Steam per recipe and per machine, fibre and fabric supplier data |
Automotive supplier | Electricity (presses, injection moulding, compressors, robots), paint and heat-treatment ovens, purchased materials | Compressed air, variable-speed drives, renewable electricity, curing ovens, recycled-content materials | Load curve, consumption per line, carbon content of purchased materials |
Cement: clinker before fuel
In a cement plant, a large share of emissions comes from the reaction itself: decarbonation of limestone in the kiln. Switching fuel does not touch these process emissions; reducing the clinker content per tonne of cement does.
Work through the levers in this order of questions:
- Clinker ratio: which additions (limestone, slag, ash, pozzolans, calcined clays) do your product standards and customers accept, and for which product ranges?
- The kiln: air tightness, preheater, cooler, stable operation, thermal consumption per tonne of clinker.
- Fuels: share of alternative fuels (prepared waste, biomass), with their analyses and traceability of the biomass fraction.
- Electricity: mills and fans, variable-speed drives, waste heat recovery for power, then renewable electricity.
Under CBAM, cement, clinker and calcined kaolinic clays (CN code ex 2507 00 80) are covered, including the electricity consumed.
Fertilisers: steam, acids and precursors
A fertiliser complex is a network of plants exchanging heat and materials. The first task is the site’s steam and material balance, line by line: without them, no reduction can be measured.
- Sulphuric acid heat: the reaction releases heat, often recovered as steam and power. Using it better reduces fuel-fired steam and purchased electricity.
- Drying and granulation: burners, temperatures, product moisture, insulation.
- N2O from nitric acid, if the site makes it: a gas with a high warming potential that dedicated catalysts reduce; it is declared under CBAM for nitric acid and nitrogen fertilisers.
- Purchased ammonia: for complex goods, Annex IV of the CBAM Regulation adds to the installation’s emissions those of the precursors listed in Annex I, including ammonia, using the value of the installation that produced them where it can be measured. Your ammonia supplier’s data therefore becomes CBAM data.
A point for exporters: fertilisers containing nitrogen and phosphorus (CN code 3105) are within CBAM, except phosphorus-potassium fertilisers (3105 60 00), while phosphoric acid and straight phosphate fertilisers are not listed. The customs classification of each product is the first check.
Steel: electricity and the reheating furnace
In a steel plant with an electric arc furnace, electricity weighs heavily; in a rolling mill, the billet reheating furnace is usually the main fuel user. The first thing to establish is your site’s production route and its consumption per heat and per rolled tonne.
Levers: arc furnace stability and efficiency (scrap preheating, oxygen, electrodes), heat recovery and combustion tuning on the reheating furnace, hot charging, renewable electricity, scrap sorting and quality. A useful CBAM nuance: iron and steel are in Annex II, so only their direct emissions are counted. Your electricity is not in the importer’s declaration, but it remains in your customers’ scope 3 and in their questionnaires.
Food and beverage: steam, refrigeration and packaging
A food plant decarbonises its utilities first: boilers and the steam network, refrigeration, compressed air. Refrigerants deserve their own line: only the top-up log can quantify leaks.
Levers: steam traps and lagging, heat recovery from refrigeration compressors and hot water, solar heat for process water, refrigerant tightness and substitution, lighter and recyclable packaging. For packaging sold in the EU, the PPWR applies: see PPWR and packaging. For the sector, see food and beverage.
Textiles: finishing heat
In spinning and weaving, electricity dominates; in dyeing and finishing, heat does (baths, drying, stenters). The first job is knowing the steam used per recipe and per machine.
Levers: heat recovery from spent baths and stenter exhaust, boiler tuning and maintenance, machine insulation, variable-speed drives, lower-temperature recipes where quality allows. For a contract manufacturer working for European brands, scope 3 is driven by purchased fibres and fabrics, and requests arrive by questionnaire: see CSRD, VSME and ESG questionnaires.
Automotive suppliers: electricity first
On an injection moulding, wiring harness, stamping or assembly site, electricity is usually the first energy use: confirm it with your own inventory. Paint and heat-treatment ovens come second.
Levers: compressed-air leak hunting and control, variable-speed drives on presses and pumps, standby management outside production, heat recovery from compressors, renewable electricity, then recycled-content materials. European carmakers ask for this data in their supplier questionnaires; our CSRD, VSME and ESG questionnaires page explains how to answer them.
What data should you collect before choosing levers?
Energy, production, process and purchasing data, at workshop level. A decarbonisation plan is first a metering exercise: a lever you cannot measure before and after cannot enter the pathway.
Data | Where to find it | What it is used for | Frequency |
|---|---|---|---|
Energy use (electricity, gas, fuel oil, petcoke, propane) | Invoices, readings, meters | Scopes 1 and 2, baseline | Monthly, over three years |
Sub-metering by workshop and use | Sub-meters, supervision system | Significant energy uses, opportunities | Continuous or weekly |
Output by product | Production system, material accounts | Intensity per tonne, CBAM data per good | Monthly |
Fuel and material analyses (calorific value, carbon content, composition) | Laboratory, supplier certificates | Site-specific emission factors, process emissions | Per batch or per monitoring plan |
Electricity load curve and contract | Grid operator, supplier | Sizing self-generation, efficiency | At meter interval, over one year |
Refrigerant inventory | Maintenance log | Fugitive emissions | Annual and at each top-up |
Tonne-kilometres by mode | Forwarders, carriers, transport software | Scope 3 transport, ISO 14083:2023 (formerly IWA 16:2015) method | Quarterly |
Purchases by category and supplier | Accounts, purchasing | Upstream scope 3, supplier engagement | Annual |
Three rules prevent most rework:
- Every emission factor carries its source and year. Otherwise a year-on-year drop may come from a factor change rather than an action.
- Output is counted like energy, with the same boundary and period. Intensity per tonne is the indicator your customers will compare.
- CBAM data is kept per installation and per good, not for the company as a whole: see CBAM for exporters.
For energy indicators, ISO 50006:2023 — Energy management systems — Evaluating energy performance using energy performance indicators and energy baselines (formerly ISO 50006:2014) gives the method: choose the indicator, normalise for output or weather, set the baseline. For transport, ISO 14083:2023 — Greenhouse gases — Quantification and reporting of greenhouse gas emissions arising from transport chain operations sets the calculation per transport chain.
In what order should actions be taken?
Measure, remove waste, improve efficiency, then change energy and process, and finally work on the value chain. This order avoids oversizing a solar plant or buying equipment that locks out electrification for its whole service life.
- Measure. Baseline inventory, sub-metering, refrigerant log.
- Remove waste. Compressed-air and steam leaks, steam traps, insulation, combustion tuning, machines idling. These actions need little investment and show results quickly.
- Improve efficiency. Variable-speed drives, motors, waste heat recovery, furnace control. An energy management system under ISO 50001:2018 — Energy management systems — Requirements with guidance for use (formerly ISO 50001:2011) provides the framework, and energy audits follow ISO 50002-1:2025 (formerly ISO 50002:2014), with ISO 50002-3:2025 for processes.
- Green the electricity. Once consumption is reduced: self-generation, renewable power bought from a private producer, certificates of origin. Sizing is based on the reduced load curve.
- Switch fuel or electrify heat, in step with equipment renewal: boiler, kiln, dryer. This is where lock-in risk is highest.
- Change process or materials. Clinker ratio, recipes, recycled materials, catalysts: these levers need trials, quality sign-off and sometimes customer approval.
- Work on scope 3. Primary data from the suppliers that weigh most, then supplier targets, logistics, ecodesign.
The order adapts to the sector. A cement plant starts low-clinker cement trials early, because product approval takes time. A plant making nitric acid studies N2O abatement early, because the lever is targeted and measured at the stack. An automotive supplier, where electricity dominates, moves quickly to step 4 once compressed air is fixed.
What does the EU CBAM change for Moroccan cement, fertiliser and steel producers?
It turns your installation’s emissions into commercial data: the EU importer declares the embedded emissions of the goods it buys, and every tonne avoided at your site reduces what it declares when it uses your actual values rather than default values.
Regulation (EU) 2023/956 establishing a carbon border adjustment mechanism (CBAM), as amended by Regulation (EU) 2025/2083, has applied in its definitive regime since 1 January 2026. Sales of CBAM certificates on the common central platform start on 1 February 2027, and an importer whose net imported mass does not exceed 50 tonnes per calendar year is exempt. In the consolidated text read on EUR-Lex on 11 November 2026:
Sector (Annex I) | Gases covered | Emissions counted (Article 7 and Annex II) |
|---|---|---|
Cement and clinker, calcined kaolinic clays | CO2 | Direct and indirect |
Fertilisers: nitric acid, potassium nitrates, nitrogen fertilisers, compound fertilisers (CN 3105, except phosphorus-potassium) | CO2 and N2O | Direct and indirect |
Fertilisers: ammonia | CO2 | Direct and indirect |
Iron and steel | CO2 | Direct only |
Aluminium | CO2 and perfluorocarbons | Direct only |
Hydrogen, electricity | CO2 | Direct only |
For a cement or fertiliser producer, this means the electricity consumed counts in the declared emissions: electrical efficiency and renewable electricity become CBAM levers, provided they are documented. For a steel producer, CBAM levers are scope 1 levers first. In every case, the operator holds the data and the importer declares it. Our article on the CBAM definitive period sets out the timeline.
Which Moroccan laws and schemes frame these actions?
Three laws frame the energy levers: Law No. 47-09 on energy efficiency, Law No. 82-21 on electricity self-generation and Law No. 13-09 on renewable energy. The decarbonisation strategy page details them; here is what they change for an industrial plan.
- Mandatory energy audit. Under Decree No. 2-17-746 of 10 April 2019, an industrial company consuming more than 1,500 tonnes of oil equivalent a year must have an audit carried out by an approved body, repeated within five years at most, and send its energy data every year to AMEE, Morocco’s national energy efficiency agency. A certified energy management system exempts the company from the audit, not from the annual data submission (Article 3). The audit report feeds the lever register directly: see ISO 50001 and energy audits.
- Self-generation. Decree No. 2-25-100 of 5 March 2026 (Official Bulletin No. 7489 of 9 March 2026, Arabic text), implementing Law No. 82-21, requires a declaration below 11 kilowatts, a grid connection agreement from 11 kilowatts to 5 megawatts and an authorisation above that. Since surplus sold to the grid is capped at 20% of annual production, the plant is sized on reduced consumption.
- Buying renewable electricity. Law No. 13-09, as amended, allows a private producer to supply grid-connected consumers for their own use.
- SME support. Maroc PME’s PACT’Décarbonation/Eau programme lists among eligible actions water, energy and environment diagnostics, substitution of energy, materials or technology, the carbon footprint and decarbonisation plan, and decarbonisation solutions for industrial sites (page read on 11 November 2026). AMEE also presents a technical assistance offer. ACG promises no funding: each scheme sets its own conditions.
How can you check that your industrial plan is sound?
Review it lever by lever with production, maintenance, purchasing and finance, and check that no figure lacks a source. A sound plan stands up to a customer audit, a lender review and a verifier.
What about climate targets and claims?
An industrial plan can set a reduction target validated by the SBTi: version 2.0 of the Corporate Net-Zero Standard was published on 11 June 2026, and version 1.3.1 remains usable until 31 January 2028. What is said to the public is more tightly framed. Since 27 September 2026, Directive (EU) 2024/825 bans claiming, on the basis of offsetting, that a product has a neutral, reduced or positive greenhouse gas impact, and requires any claim of future environmental performance to rest on a detailed, realistic plan verified by an independent third party. Carbon neutrality is demonstrated under ISO 14068:2026 (formerly ISO 14068-1:2023), which puts reduction before offsetting: see carbon neutrality ISO 14068 and our article on Directive (EU) 2024/825. Our position: avoided tonnes first, claims second, and only when substantiated.
When a customer asks for the footprint of a product rather than of the site, you need a product carbon footprint under ISO 14067:2018 (under revision, draft ISO/WD 14067.2 at stage 20.60 on iso.org on 11 November 2026): see our ISO 14067 guide.