circular-economy · energy · family: the missing yardstick
one powder, two passports
The same shredded-battery powder is "Hazardous Waste" leaving Europe and a "Recycled raw Material" arriving in China — and nobody has written the physical specification that would let regulators agree on what it is
Problem statement
When a lithium-ion battery is shredded, the cathode and anode coatings come off as a black powder — "black mass" — that holds the nickel, cobalt, lithium and graphite worth recovering. Making black mass is easy ("low barrier to entry with low CAPEX investment and limited technology hurdles," per RECHARGE); refining it into battery-grade salts is hard and capital-intensive, and China holds most of that capacity ("85% of worldwide refining capacity," of which "70-80% ... currently idle," per the Beveridge & Diamond analysis). Regulators have now written opposite rules for the same material. The EU's Commission Delegated Decision (EU) 2025/934 adds List of Wastes code 19 14 02 for the intermediate fraction from treating lithium batteries and classifies it as hazardous, so under the Waste Shipment Regulation "EU countries will be prohibited from sending black mass to non-OECD countries"; China, which had banned black-mass imports as hazardous waste for years, issued national standard GB/T 45203-2024 (effective 1 July 2025) and a June 2025 announcement under which black mass meeting compositional grades is non-waste and "can be imported freely (i.e., without any waste restrictions) into China from any other country that classifies the material as non-waste or non-hazardous" from 1 August 2025 — a qualifier that itself excludes EU-origin material once the EU code applies; the United States classifies it as hazardous waste unless it passes the TCLP leaching test. Beneath the policy fight lies a technical vacuum: there is no internationally shared physical definition, sampling protocol or assay standard for black mass, so "hazardous" and "raw material" are being applied to a heterogeneous powder whose properties nobody measures the same way. RECHARGE's own first ask is "a better and standardised definition of Black Mass."
Why this matters
Black mass is the strategic hinge of battery circularity: whoever refines it captures the critical minerals, and whoever cannot must import them again. Europe's recycling base "mainly consists of pre-processing operators; whereas post-treatment or 'refining' of Black Mass activities takes place outside the EU," so most European black mass "leaves EU to be refined elsewhere, mainly in South-East Asia." China's recyclers, per Fastmarkets, run at "less than 50%" utilisation and want feedstock; a Southeast Asian trader warned that GB/T 45203's impurity limits (copper ≤0.5 percent, aluminium ≤1 percent, moisture <2 percent, iron ≤0.5–1 percent depending on grade) are "extremely strict ... It will be very hard for black mass from scrapped batteries to meet standards." The result is a thin, volatile market in which the same tonne can be stranded, re-graded or re-routed depending on which customs officer reads which code, recyclers cannot plan refining investments, and the Basel Convention parties agreed at COP-17 (April–May 2025) to prioritise negotiations on hazardous-waste scope with a decision expected at COP-18 in 2027. The EU's amended List of Wastes becomes mandatory on 9 November 2026. In the meantime black mass moves under conflicting paperwork or sits in warehouses.
What’s been tried and why it hasn’t worked
Each jurisdiction has solved the problem for itself. China's GB/T 45203-2024 is the first national specification: two types (Type 1 from nickel/cobalt chemistries in three grades by Ni+Co and Li content; Type 2 from LFP with >2 percent Li) with universal impurity caps — but it is written to admit refinable feedstock, not to assess hazard, and its thresholds exclude much real scrap-derived material. The EU has defined black mass by process origin (a code for "the intermediate fraction from thermal/mechanical treatment of waste lithium-based batteries") and by hazard, without a compositional specification, and its Battery Regulation delegated acts on recycling efficiency and material-recovery calculation — the rules that would define what counts as recycled — were, per RECHARGE, still to be issued "without further delay" in 2025. The United States relies on a leaching test designed for landfill risk, not for a reactive powder that may contain lithium metal, fluorinated electrolyte residues and fine graphite. Industry associations (RECHARGE, and in the US ReMA's scrap specifications) have proposed definitions, but each is shaped by where its members want the material to flow: European producers want a definition strict enough that "no BM inadvertently becomes classified as a product," Chinese refiners want one loose enough to import. Because the parties disagree on the goal — retain versus attract — no shared characterisation framework has been commissioned, and the physical questions (particle-size distribution, residual electrolyte and fluorine, moisture and reactivity, heavy-metal leachability, sampling of a segregating powder) go unanswered in the regulatory texts.
What would unlock progress
A jurisdiction-neutral characterisation and sampling standard for black mass — one that reports the hazard-relevant properties (reactivity, fluorine/HF potential, leachable metals, dust) and the value-relevant ones (Ni/Co/Li/graphite content, Cu/Al/Fe impurities) on the same certificate — would let each regulator apply its own policy to a shared measurement, the way ISO alloy specifications let steel scrap trade under different national waste rules. Digital battery passports and the EU's forthcoming calculation methodologies could carry that certificate with the shipment. The adjacent precedent is e-waste and copper-bearing scrap, where Basel technical guidelines and industry specifications (ISRI/ReMA grades) coexist: policy divergence remained, but the physical descriptions converged enough for shipments to be adjudicated consistently.
Entry points for student teams
A materials/analytical team could obtain black-mass samples (several recyclers and universities hold them) and develop a reproducible sampling-and-assay protocol for a segregating fine powder — testing how much reported Ni/Co/Li and impurity values swing with sampling method — and compare results against the GB/T 45203 grade thresholds and EU hazard criteria (H-codes for reactivity, toxicity, leaching). A policy-design team could draft a mapping between the GB/T grades, the EU 19 14 02 hazard classification and the US TCLP outcome for the same characterised samples, showing exactly where the regimes disagree and whether a shared certificate could resolve it. An economics team could model the arbitrage and stranded-volume effects of the divergence for one recycler under the 2026 EU and 2025 China rules. Relevant skills: analytical chemistry, hazardous-materials regulation, trade law, techno-economic modelling.
Genome — every gene is a door
Structural cousins — same reason stuck, other fields
Sources
Goldberg, A.H., Hagen, P.E., Luo, W. (Beveridge & Diamond PC) (21 July 2025), "China and Europe Diverge on Classification of Black Mass from Recycling of Lithium-Ion Batteries," *National Law Review*, accessed 2026-08-18. Supplementary: RECHARGE (March 2025), "Fostering a resilient European battery value chain through closing the loop for battery materials: A Whitepaper on Black Mass," accessed 2026-08-18; Fastmarkets (14 January 2025), "China's first national standards for black mass could help open import market, sources say," accessed 2026-08-18. go to source 1 ↗ go to source 2 ↗ go to source 3 ↗
verification notes (working record)
The collection team’s own sourcing notes for this brief, kept verbatim:
Regulatory facts and quotations (Delegated Decision (EU) 2025/934 entered into force 19 June 2025; code 19 14 02; List of Wastes mandatory 9 November 2026; China's 10 June 2025 announcement and 1 August 2025 import opening; "85% of worldwide refining capacity ... 70-80% ... idle"; TCLP; Basel COP-17 dates and COP-18 expected April 2027) are from a WebFetch summary of the National Law Review article dated 21 July 2025 (the Beveridge & Diamond original returned HTTP 403); the verifier re-fetched the National Law Review page and restored the full China-import quotation, whose qualifier ("from any other country that classifies the material as non-waste or non-hazardous") had been truncated. GB/T 45203-2024 and its 1 July 2025 effective date come from the Fastmarkets article, not the National Law Review piece. GB/T 45203-2024 grade thresholds, the "less than 50%" utilisation figure and the trader quote are from a WebFetch summary of the Fastmarkets article; the standard itself was not read. RECHARGE quotations ("low barrier to entry"; "mainly consists of pre-processing operators"; "mainly in South-East Asia"; the standardised-definition ask; delegated acts "without further delay") are from the whitepaper PDF read in full. The reference to ReMA scrap specifications is the author's characterisation and was not verified this session; the physical-hazard list (lithium metal, fluorinated electrolyte, graphite dust) is general battery-recycling knowledge, not from the fetched sources. This is a regulatory-divergence problem, so `constraint:coordination` was explicitly tested and rejected on filter (1): the EU and China do not agree on the desired outcome (retain versus attract black mass), so it is not willing parties failing to coordinate — hence `constraint:regulatory` and `failure:regulatory-mismatch`. `constraint:supply-chain` is applied because refining capacity is concentrated in one geopolitical actor, which is what makes the classification consequential. `temporal:window` is a deadline window (EU List of Wastes mandatory Nov 2026; Basel COP-18 2027). `stakeholders:multi-institution` passes: the Commission, Chinese ministries, Basel parties and recyclers each own a non-substitutable piece. Related collection brief: `energy-lfp-battery-recycling-economics` (why LFP is uneconomic to recycle — a different, economic problem); this brief is the classification/specification gap for the intermediate product.
Source type: Observed (legal analysts and an industry association describing a regulatory divergence; the missing characterisation standard is the author's synthesis of their stated asks)
Verified at intake 2026-08-18: gate (net) + adversarial source check + contested-tag second coding.
Related briefs (distinct sub-problems, cross-referenced 2026-08-18): `energy-ev-battery-passport-state-of-health-measurement-gap`, `energy-lfp-battery-recycling-economics`.