Lead battery recycling spans municipal waste flows, industrial mass balances, automotive battery categories and European process-efficiency rules. The figures below keep those populations, periods and definitions separate so recovery rates are not confused with collection rates or regulatory targets.
Key Lead Battery Recycling Statistics
The most useful headline figures include:
- In 2018, 2,870 thousand U.S. tons of lead-acid batteries were recycled in the EPA’s municipal-solid-waste estimate for automotive, truck and motorcycle batteries.
- In 2018, 2,900 thousand U.S. tons of U.S. lead-acid batteries were generated in the EPA MSW estimate, equal to 1.0% of total MSW generation.
- In 2018, 30 thousand U.S. tons of lead-acid batteries were landfilled in the EPA estimate.
- During 2017–2021, BCI estimated a 101.0% U.S. battery-lead recycling rate for SLI, industrial and small sealed lead batteries.
- During 2017–2021, 12,210,065,090.3 pounds of battery lead were recycled by U.S. secondary lead recyclers, according to BCI’s worksheet.
- During 2017–2021, 12,090,446,953.15 pounds of U.S. battery lead were available for recycling in BCI’s derived mass balance.
- During 2017–2021, 18,973,460,309 pounds of lead were in batteries consumed domestically in the United States, according to BCI’s estimate.
- During 2017–2021, 444,527,596 passenger-car and light-truck batteries were consumed domestically in BCI’s U.S. automotive calculation.
- During 2017–2021, 10,920,694,651 pounds of lead were in passenger-car and light-truck batteries consumed domestically, based on BCI’s modeled units and average weight.
- During 2017–2021, 53,906,701 heavy-truck batteries were consumed domestically in BCI’s U.S. estimate.
- During 2017–2021, 35,436,414 marine and RV batteries were consumed domestically in BCI’s U.S. estimate.
- In 2023, all EU countries with reported data achieved at least the 65% lead-acid recycling-efficiency target in the Eurostat series.
- In 2023, three EU countries reported lead-acid recycling efficiencies above 90%: Hungary, Italy and Slovakia.
- In 2023, 15 EU countries reported lead-acid recycling efficiencies from 80% to 90%.
- In 2023, eight EU countries reported lead-acid recycling efficiencies from 70% to 80%.
- EU portable-battery collection rose from 35% in 2012 to 44.1% in 2016 in the Commission evaluation series.
- In 2016, 14 EU Member States met the 45% portable-battery collection target.
- By the end of 2025, the EU lead-acid recycling-efficiency target is 75% by average weight, a regulatory target rather than an observed result.
- By the end of 2030, the EU lead-acid recycling-efficiency target is 80% by average weight, a regulatory target rather than an observed result.
Contents
- U.S. lead battery generation and recovery
- U.S. lead battery recycling trends
- Battery lead rates and recovered quantities
- Automotive lead battery scale and weights
- European lead-acid efficiency statistics
- European collection and recycling targets
U.S. Lead Battery Recycling Statistics by Generation and Recovery
The EPA series is a U.S. municipal-solid-waste material-flow estimate for automotive, truck and motorcycle lead-acid batteries. It is not a global recovery rate and does not represent every lead-acid battery sold nationally.
| Year | Generated (thousand U.S. tons) | Recycled (thousand U.S. tons) | Landfilled (thousand U.S. tons) |
|---|---|---|---|
| 1970 | 820 | 620 | 200 |
| 1980 | 1,490 | 1,040 | 450 |
| 1990 | 1,510 | 1,470 | 40 |
| 2000 | 2,280 | 2,130 | 150 |
| 2005 | 2,750 | 2,640 | 110 |
| 2010 | 3,020 | 2,980 | 40 |
| 2015 | 2,700 | 2,670 | 30 |
| 2017 | 2,940 | 2,910 | 30 |
| 2018 | 2,900 | 2,870 | 30 |
Source: Durable Goods: Product-Specific Data, EPA material-flow estimates.
The categories are measured in thousand U.S. tons, and the recycling total includes recovered lead, polypropylene and removed electrolytes or other materials. EPA also notes that lead-acid batteries are not accepted at combustion facilities, which helps explain why the disposal category is reported as landfilling in this series.
Lead-Acid Battery Recycling Trends in U.S. Material Flows
The long-run EPA estimates show both a larger material stream and a smaller landfill stream in the reported years. Generation reached 3,020 thousand U.S. tons in 2010 before standing at 2,900 thousand U.S. tons in 2018, while landfilling was 30 thousand tons in both 2017 and 2018.
- In 1970, the EPA estimated 820 thousand U.S. tons generated, 620 thousand recycled and 200 thousand landfilled in U.S. MSW.
- In 1980, the corresponding estimates were 1,490 thousand generated, 1,040 thousand recycled and 450 thousand landfilled.
- In 1990, the estimates were 1,510 thousand generated, 1,470 thousand recycled and 40 thousand landfilled.
- In 2000, the estimates were 2,280 thousand generated, 2,130 thousand recycled and 150 thousand landfilled.
- In 2005, the estimates were 2,750 thousand generated, 2,640 thousand recycled and 110 thousand landfilled.
- In 2010, the estimates were 3,020 thousand generated, 2,980 thousand recycled and 40 thousand landfilled.
- In 2015, the estimates were 2,700 thousand generated, 2,670 thousand recycled and 30 thousand landfilled.
- In 2017, the estimates were 2,940 thousand generated, 2,910 thousand recycled and 30 thousand landfilled.
The 2018 estimate places lead-acid batteries at 1.0% of total U.S. MSW generation. These are EPA estimates for the defined MSW stream, so they should not be presented as a national percentage for all battery transactions or as a worldwide trend.
Source: Durable Goods: Product-Specific Data.
Battery Lead Recycling Rates and Recovered Lead Quantities
BCI’s National Recycling Rate Study uses a U.S. mass-balance approach covering SLI, industrial and small sealed lead batteries during 2017–2021. Its calculated 101.0% rate is an estimate over the study period, not a claim that more than 100% of every individual battery was recycled.
| BCI measure | 2017–2021 estimate | Definition or limitation |
|---|---|---|
| Lead in domestically consumed batteries | 18,973,460,309 lb | Shipment, trade and battery-weight inputs |
| Battery-scrap lead imports | 83,760,218 lb | Trade component |
| Battery-scrap lead exports | 6,966,773,574.1 lb | Trade component |
| Lead available for recycling | 12,090,446,953.15 lb | Derived from consumption plus imports minus exports |
| Lead recycled | 12,210,065,090.3 lb | Whole batteries and battery scrap received by recyclers |
BCI reported a standard deviation of ±0.3 percentage points around the 101.0% study-period estimate. Its 10-year trailing U.S. battery-lead recycling average ending in 2021 was 99.8%, using current and prior BCI National Recycling Rate Studies.
The study also estimated 16,048,302,317 pounds of lead in automotive batteries consumed domestically, 1,534,437,599 pounds in motive-power batteries and 664,022,862 pounds in stationary batteries over 25 Ah. BCI says its worksheet groups categories and applies estimated lead weights, and that recycler questionnaires record receipts by weight.
Source: National Recycling Rate Study, Battery Council International and Vault Consulting.
Automotive Lead Battery Recycling Scale and Battery-Weight Data
BCI’s automotive calculation gives unit and lead-weight context for the five-year U.S. period from 2017 through 2021. The weights are category averages used in the study model, not measurements of every battery.
| Automotive category | Batteries consumed | Average lead weight | Estimated lead consumed |
|---|---|---|---|
| Passenger-car and light-truck | 444,527,596 | 24.57 lb | 10,920,694,651 lb |
| Truck and heavy-duty truck | 53,906,701 | 39.32 lb | 2,119,480,938 lb |
| Marine and RV | 35,436,414 | 27.75 lb | Not reported in the supplied calculation |
The passenger-car and light-truck estimate is the largest listed automotive unit category, while the heavy-truck category uses the highest supplied average lead weight. The marine and RV count is a modeled cohort based on shipments and trade flows, as are the other automotive unit totals.
The automotive values are part of BCI’s U.S. study calculation and should not be combined directly with the EPA MSW series: the sources use different populations, methods and reporting frames. BCI also says it cannot determine recycling rates by battery category from its recycler data.
Source: National Recycling Rate Study.
European Lead-Acid Battery Recycling Efficiency Statistics
Eurostat’s process-efficiency measure is distinct from a collection rate. For the EU series, the lead-acid recycling-efficiency target was 65% by average weight, and every EU country with 2023 data met at least that target.
| 2023 EU reported efficiency | Number of countries | Named countries where supplied |
|---|---|---|
| Above 90% | 3 | Hungary, Italy and Slovakia |
| 80% to 90% | 15 | Not listed in the supplied facts |
| 70% to 80% | 8 | Not listed in the supplied facts |
| 65% to 70% | 1 | Estonia |
The country comparison covers EU countries reporting 2023 data, with reporting gaps and estimated values noted in the Eurostat material. It therefore describes reported coverage rather than proving that missing-data countries met the same thresholds.
Source: Waste statistics — recycling of batteries and accumulators.
Lead Battery Collection and Recycling Targets in Europe
The Commission’s historical collection series concerns EU portable batteries, not automotive lead-acid batteries. Portable-battery collection rose from 35% in 2012 to 44.1% in 2016, while portable batteries placed on the market increased from 209 thousand tons to 215 thousand tons.
| Portable-battery measure | 2012 | 2016 |
|---|---|---|
| Placed on the market | 209 thousand tons | 215 thousand tons |
| Waste collected | 75 thousand tons | 94 thousand tons |
| Collection rate | 35% | 44.1% |
| EU collection target | 25% | 45% |
Fourteen EU Member States met the 45% portable-battery collection target in 2016. These collection figures should not be treated as lead-acid process-efficiency results because automotive and industrial batteries are not included in the portable-battery sales and collection denominators.
The Batteries Regulation sets future lead-acid recycling-efficiency targets of 75% by average weight at the end of 2025 and 80% at the end of 2030. Those are regulatory targets, not observed results; separate EU material-recovery targets for lead, cobalt, copper and nickel are 90% by the end of 2027 and 95% by the end of 2031.
Sources: Evaluation of the Batteries Directive; Recycling of Critical Minerals — Executive Summary.