Matrix Pathways for Credits

How compost blends, co-composting, and soil application sit inside voluntary biochar CDR methodologies and US practice payments—cross-links only. Deep methodology chapters stay in Carbon Markets; this note maps application-matrix choices growers and project developers actually face. Do not use this note as a substitute for Puro Biochar Methodology Edition 2025, Verra VM0044, Isometric Biochar Protocol, or MRV Stack.

Report context: 2026-09-16. Out of scope here: CSI deep rewrite (other stream); permanence science deep rewrite (Permanence, Permanence Science for Credits remain the homes).


1. Two different money streams

StreamWhat it pays forBiochar–compost relevancePrimary URL
NRCS CPS 336 (EQIP/CSP etc.)Practice cost-share for soil carbon amendmentBlend scenarios (biochar ± compost quantities); inoculate language; not a carbon credithttps://nrcs-prod.azureedge.us/sites/default/files/2026-04/soil-carbon-amendment-ac-336-faq.pdf · answers CPS 336 planning questions
Voluntary CDR (Puro / Verra / Isometric / …)Eligible durable biochar C after eligible end-useSoil amendment pure or mixed often eligible; quantification follows methodology persistence rules on biochar C, not compost CRegistry/methodology links below

A text search framing in vault notes: CPS 336 FAQ does not discuss carbon credits as part of the practice (FAQ). Stacking requires explicit ownership / no-double-claim language (Double Counting and Credit Ownership).


2. Soil / agriculture end-use families (pointers)

Puro.earth

Verra VM0044

Isometric

Comparison hub

Verra vs Isometric vs Puro · Carbon Markets Hub · Biochar as Durable CDR.


3. Does co-composting erase permanence?

No — not in the chemistry framing used by this vault. Hagemann et al. (2017) find co-composting does not substantially change bulk carbon speciation; aromatic stability underpinning persistence is not erased by the organic coating (DOI). Credit quantification still follows each methodology’s persistence / F_perm / monitoring rules on measured biochar carbon (Permanence, models soil GHG from biochar · DOI; Permanence Science for Credits, MRV Stack).

NRCS FAQ contrast (practice education, not a credit equation): roughly 60–80% of biochar C remaining at 100 years vs 2–14% of compost C in their cited research summary (FAQ). Do not paste that FAQ range into a credit calculator without the methodology’s own tables.


4. What composting-process GHG cuts are not

Facility reductions such as:

  • Earth Foundries non-methane VOC −33% at 10% v/v biochar (PDF),
  • Composting CH₄/N₂O/NH₃ metas (e.g. Li et al. 2025 mean CH₄ −53.7%, N₂O −49.8%, NH₃ −35.9% — DOI),

are process-boundary benefits. They are not automatically soil-storage CORCs and are not interchangeable with Woolf’s optional soil N₂O inventory term (Nitrous Oxide Fluxes, GHG Fluxes, models soil GHG from biochar). Separate MRV if claiming facility emission reductions under a different instrument.


5. Grower / developer checklist

  1. Decide end-use evidence early (soil application records, GPS, invoices, photos per methodology).
  2. Keep batch identity of biochar (feedstock, T, lab sheet, mass) through co-composting so biochar C remains auditable.
  3. State whether compost is a carrier/inoculant vs a separately claimed soil-C practice.
  4. If CPS 336 cost-share is used, put CDR ownership in writing (Double Counting and Credit Ownership).
  5. Do not budget multi-year soil N₂O co-benefits into credit NPV unless the methodology explicitly credits them—and most biochar CDR tonnage is stable C, not flux (GHG Fluxes, Agronomic Economics).