Methane Emissions from the LNG Chain

Methane (CH₄) is both the main constituent of LNG and one of its largest climate concerns. Methane has a much higher warming potential than CO₂ on short timescales, so small amounts released along the value chain have outsized effects on the near-term climate footprint. Understanding where methane escapes, how accurately it is measured, and what reduction looks like in practice is essential to any honest discussion of LNG's environmental profile.

Why methane matters more than its share suggests

Methane is roughly 80–85 times more potent than CO₂ as a greenhouse gas on a 20-year timescale and about 28–30 times more potent over 100 years (IPCC values vary slightly across assessment reports). Its atmospheric lifetime is short — around a decade — so reducing methane emissions produces near-term climate benefits that CO₂ reductions cannot match.

For LNG, this has a specific consequence: the climate advantage of gas over coal at end use depends heavily on how much methane escaped on the way to the burner tip. Published peer-reviewed studies show that once upstream leakage rises above roughly 3% of production, the 20-year climate case for LNG against coal weakens substantially. Below that threshold, gas retains a clear climate advantage. This is why leakage rate, not just combustion emissions, is the first number asked about in any serious lifecycle assessment.

Where methane escapes along the chain

1. Upstream production

The biggest source of methane emissions is typically the upstream end of the chain — well sites, gathering lines, and early-stage processing. Sources include:

  • Pneumatic controllers that use gas pressure to actuate valves, venting small volumes of methane continuously.
  • Unlit flares and flare inefficiency, which release unburned methane when combustion is incomplete.
  • Liquids unloading and well workovers, which vent gas when clearing wellbore liquids.
  • Storage tank venting from flash gas and working/breathing losses.
  • Equipment leaks — valves, flanges, connectors, compressor seals.
  • Super-emitters: a small number of malfunctioning or poorly maintained sites responsible for a disproportionate share of total emissions.

2. Gathering, processing, and transmission

Between the wellhead and the liquefaction plant, methane can escape from compressor stations, processing plants, and long-distance pipelines. Compressor-seal leakage and pneumatic venting are recurring contributors. Maintenance events and unplanned equipment failures are also important.

3. Liquefaction

At the export plant, methane emissions are generally lower as a share of throughput than upstream, but still non-zero. Sources include turbine and engine slip (unburnt methane in exhaust), vented boil-off gas when combustion is not practical, and leaks from valves, flanges, and storage tank vents.

4. Shipping

LNG carrier engines burn boil-off gas as fuel. Older slow-speed dual-fuel engines had significant methane slip — unburnt methane in the exhaust — under certain load conditions. Newer engine designs and controls have reduced slip substantially; the industry trajectory is toward engines with methane slip well below 1%. Onboard reliquefaction also avoids venting by returning vapourised cargo to the tank.

5. Regasification and downstream distribution

Regasification terminals contribute a small share. Most downstream distribution emissions occur in low-pressure gas distribution networks in the end market — particularly older networks with cast-iron or unprotected steel mains.

How methane is measured

Historically, national inventories relied on bottom-up emission factors: estimate the number of components (valves, pumps, compressor seals), multiply by a standard leak rate, and sum. Research over the past decade has repeatedly shown that bottom-up methods can underestimate actual emissions — sometimes substantially — because they do not capture super-emitters and episodic releases.

Top-down measurement methods address that gap:

  • Aircraft and drone surveys measure methane concentrations downwind of facilities and use atmospheric dispersion models to back out emission rates.
  • Satellites such as TROPOMI (global but lower resolution), GHGSat (facility-level), and MethaneSAT detect methane plumes at increasing spatial detail. Carbon Mapper integrates several data sources to track super-emitters globally.
  • Continuous monitoring using fixed sensors on tall towers or at facility fences is becoming more common at newer sites.
  • OGI (optical gas imaging) cameras are widely used for leak detection and repair (LDAR) programmes, making otherwise invisible methane visible in infrared.

Each approach has strengths and limitations. Bottom-up inventories give component-level detail; top-down surveys capture the total including super-emitters but can miss small continuous leaks. The practical state-of-the-art combines both with facility-level reconciliation.

What reduction looks like in practice

Most methane reductions along the LNG chain come from a relatively compact set of measures:

  • Replacing gas-driven pneumatics with electric or compressed-air alternatives, eliminating a continuous vent stream.
  • Leak detection and repair (LDAR) using OGI cameras at defined inspection intervals, with rapid repair of identified leaks.
  • Flare efficiency programmes, ensuring flares remain lit and combust completely; this is a large potential reduction because poorly operating flares can be major emitters.
  • Vapour recovery units on storage tanks, capturing flash and working losses for use as fuel or sales gas.
  • Compressor-seal upgrades that reduce continuous leakage, often with payback from recovered gas.
  • Low-slip marine engines and onboard reliquefaction on new-build LNG carriers.
  • Continuous monitoring to detect and address super-emitter events quickly rather than quarterly.

Policy frameworks and commitments

Several public policy frameworks now target LNG-relevant methane emissions:

  • The Global Methane Pledge, signed by a large group of countries, aims for a collective 30% reduction in methane emissions below 2020 levels by 2030.
  • EU Methane Regulation sets measurement, reporting, verification, and LDAR requirements for oil and gas operations serving the European market, including imported LNG.
  • U.S. EPA methane rules impose standards on new and existing oil and gas infrastructure, including a scheduled methane waste charge under the Inflation Reduction Act.
  • OGMP 2.0 (Oil and Gas Methane Partnership), coordinated by UNEP, is the main voluntary framework for companies committing to measurement-based reporting and ambitious reduction targets.

These policies are still maturing. Reporting rigor, coverage of upstream supply chains outside the importing country's jurisdiction, and enforcement mechanisms vary widely.

Last reviewed on April 23, 2026. Warming-potential values and leakage-rate thresholds are drawn from publicly available IPCC assessments and peer-reviewed lifecycle studies; verify current figures via the primary source relevant to your use case.