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See LCA studies →Where the energy and raw materials for 1 kg of sodium hydroxide come from: salt, coal, natural gas and fuel oil, each with its own transport and fuel inputs.


Two chemicals can do the same job and still leave very different footprints. The difference comes from how each one is made: which raw materials go in, how much energy the process draws, and what ends up in the air, water and soil along the way.
Life cycle assessment (LCA) puts numbers on that. Under ISO 14040 and 14044, it follows a product from raw material extraction through production, use and disposal, and adds up the energy used, the emissions released and the impacts they cause.
LCA results take some effort to read, but they are what decisions on chemical production should rest on. A worked example is the quickest way to see how the pieces fit, which is what this case study is for.
Pure sodium hydroxide is a white solid. It dissolves readily in water, splitting into sodium ions (Na⁺) and hydroxide ions (OH⁻), and it pulls moisture and carbon dioxide out of the air if left open. Between 12.3 and 61.8 °C, water solutions crystallise as the monohydrate, NaOH·H₂O, and much of the “sodium hydroxide” sold commercially is in fact this monohydrate.
In practice, most users buy it as a solution rather than a solid. It is cheaper to ship and far easier to pump, dose and mix.
Sodium hydroxide breaks down proteins at room temperature. It causes severe chemical burns on skin, can permanently damage eyes, and is dangerous if swallowed.
Almost all of it comes from the chlor-alkali process. An electric current is passed through salt brine, and the brine splits into three products at once.
The ratio never changes. For every tonne of chlorine, a plant makes about 1.1 tonnes of caustic soda and 0.03 tonnes of hydrogen. The industry calls this bundle an electrochemical unit, or ECU.
Because chlorine, hydrogen and caustic soda share one cell, an LCA has to decide how to split the burden between them. That choice, called allocation, can shift the result for 1 kg of sodium hydroxide considerably.
Few people handle caustic soda directly, but most use products that needed it somewhere in their supply chain. The shares below are approximate global figures; sources and regions differ.
The Bayer process uses it to dissolve alumina out of bauxite ore, the first step toward aluminium metal.
Kraft pulping uses it to break down wood chips and free the fibres. Bleaching and effluent treatment use more.
Neutralising acids, adjusting pH, and making intermediates such as propylene oxide, polycarbonates and a long list of sodium salts.
Hard bar soap is made with sodium hydroxide. Liquid soap uses potassium hydroxide instead.
Viscose rayon production, and mercerising cotton, which strengthens the fibre and helps it take dye.
Added to drilling mud to raise alkalinity and neutralise acid gases such as hydrogen sulfide and carbon dioxide. Refiners also use caustic washing to strip hydrogen sulfide and mercaptans from crude; the spent caustic is hazardous waste.
Degreasing metal parts, and adjusting pH, together with hydrochloric acid, in neutral salt spray corrosion tests.
Peeling fruit and vegetables, curing olives and giving pretzels their dark crust; it is food additive E524. At home, it is the active ingredient in many drain and oven cleaners.
The assessment models sodium hydroxide, production mix, at plant, with 1 kg of product as the functional unit. Four supply chains feed it, each shown as a stage in the product system diagram at the top of this page.
Before any number is calculated, an LCA has to answer three questions: what exactly is being measured, where the study stops, and how the load is shared when one process makes more than one product. This section answers all three for sodium hydroxide.
The study follows the four phases set out in ISO 14040 and 14044: goal and scope, inventory analysis, impact assessment and interpretation. The sections below cover the scope. Results follow later in the case study.
All calculations in this case study were carried out in Microsoft Excel, working stage by stage through the product system shown in the diagram at the top of this page.
The boundary is drawn around everything needed to get 1 kg of sodium hydroxide to the plant gate. What happens to the product after it leaves the plant is outside the scope.
| Stage | Energy and fuels | Extraction and processing | Transport |
|---|---|---|---|
| 1. Sodium chloride at plant | Diesel, bituminous coal and natural gas burned in industrial boilers; grid electricity (US) | – | – |
| 2. Bituminous coal, combusted in industrial boiler | Gasoline burned in equipment | Coal mining | Combination truck, diesel train |
| 3. Natural gas, combusted in industrial boiler | – | Natural gas processed at plant | Combination truck, diesel train |
| 4. Residual fuel oil, combusted in industrial boiler | – | Residual fuel oil at refinery | Barge, diesel train, combination truck |
Allocation is the rule for dividing emissions and energy between products that come out of the same process. Inside the four supply chains, it is not needed: each process hands a single product to the next step, so its full burden travels with that product.
The last step is different. The electrolysis cell never makes caustic soda on its own; chlorine and hydrogen come out with it, always in the same ratio. The burden of that step is therefore split between the three products by mass.
In plain terms: sodium hydroxide carries a little over half of what the cell room emits. Switch to a split by economic value and that share moves with market prices for chlorine and caustic soda, which is why the rule has to be stated up front.
This case study is published for demonstration and learning. The results are not intended for commercial use, such as product claims or procurement decisions. They may be cited in academic reports and papers.
DEISO runs cradle-to-gate and cradle-to-grave LCAs and product carbon footprints for chemical producers. Tell us the product, the site and what you need the result for.
Just over half of the 1.05 kg CO₂ eq arises at the sodium hydroxide plant itself. The other 45% is spread across the four supply chains, and the natural gas chain is the largest of them, at about a quarter of the total.
The table shows each source’s share of every impact category. Darker cells mean a bigger share. Two things stand out: the plant dominates ozone depletion and soil toxicity, and all of the mineral resource use comes from the salt stage.
Scroll sideways to see all eleven categories.
| Source | ADP elements | ADP fossil | AP | EP | FAETP | GWP | HTP | MAETP | ODP | POCP | TETP |
|---|---|---|---|---|---|---|---|---|---|---|---|
| Sodium hydroxide plant, direct | 0% | 54% | 56% | 68% | 31% | 55% | 45% | 72% | 99% | 68% | 92% |
| Sodium chloride | 100% | 13% | 11% | 11% | 24% | 13% | 17% | 11% | 0.3% | 9.6% | 2.7% |
| Natural gas, combusted in boiler | 0% | 27% | 27% | 12% | 41% | 25% | 33% | 10% | 0% | 19% | 0.3% |
| Bituminous coal, combusted in boiler | 0% | 5.5% | 6.0% | 8.0% | 0.8% | 6.8% | 3.5% | 5.9% | 0.8% | 3.8% | 5.2% |
| Residual fuel oil, combusted in boiler | 0% | 0.6% | 0.3% | 0.9% | 3.2% | 0.7% | 1.7% | 0.8% | 0% | 0.4% | 0.1% |
After normalisation and weighting, all eleven categories can be added into one score. On that single score, the plant accounts for 70%, and the salt and natural gas chains for about 12% each.
Transport is small in every chain. The largest single transport step, the diesel train carrying coal, stays under 0.1% of the weighted score.
| Process | Share of weighted score |
|---|---|
| Sodium hydroxide plant, direct | 69.9% |
| Sodium chloride | 12.0% |
| Diesel, combusted in industrial boiler | 3.6% |
| Bituminous coal, combusted in industrial boiler | 2.5% |
| Natural gas, combusted in industrial boiler | 2.4% |
| Salt production, direct | 3.6% |
| Natural gas, combusted in industrial boiler | 11.5% |
| Combustion and gas supply, direct | 11.2% |
| Transport, combination truck | 0.23% |
| Transport, diesel train | <0.01% |
| Bituminous coal, combusted in industrial boiler | 5.7% |
| Combustion, direct | 5.4% |
| Bituminous coal at the mine | 0.24% |
| Transport, diesel train | 0.07% |
| Transport, barge | 0.01% |
| Transport, combination truck | <0.01% |
| Residual fuel oil, combusted in industrial boiler | 0.84% |
| Combustion and refinery supply, direct | 0.84% |
| Transport, barge | <0.01% |
| Transport, combination truck | <0.01% |
| Transport, diesel train | <0.01% |
Normalisation compares each result with a reference level of impact, and weighting then sets how much each category counts. Once that is done, one category towers over the rest.
This is typical of CML results: marine ecotoxicity often dominates once results are weighted. Read the weighted score alongside the category results in Table 1, not instead of them. A 0.66% weighted share does not make 1.05 kg CO₂ eq per kg a small number for a buyer tracking its carbon footprint.
This case study is published for demonstration and learning. The results are not intended for commercial use, such as product claims or procurement decisions. They may be cited in academic reports and papers.
DEISO runs cradle-to-gate and cradle-to-grave LCAs and product carbon footprints for chemical producers. Tell us the product, the site and what you need the result for.
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