Framework Overview
NOAA-TDC Dual-Flow ESG Attribution Framework
The NOAA-TDC Dual-Flow Framework is a science-based methodology for quantifying the ecosystem service value (ESV) of US oyster aquaculture leases. Developed by the NOAA Technology Development Center in collaboration with Oceanfarmr, it supports ESG reporting for oyster farmers, investors, and regulators. The framework is currently operational for two regions: Virginia (Chesapeake Bay) and Maine (Gulf of Maine).
The framework operates across two parallel analytical flows — Latent Potential and Realized Contribution — which together produce a lease-level ESV estimate that is both scientifically grounded and practically useful for ESG disclosure. Each flow draws on a distinct set of data inputs and produces outputs combined through a Data Adequacy Factor (DAF) derived from the REDQS scoring system.
Architecture
Dual-Flow Architecture
The two analytical flows address a fundamental challenge in aquaculture ESG accounting: the gap between what a lease could produce (its latent potential, based on area and biophysical context) and what it actually produces (its realized contribution, based on verified harvest and water quality data). Most leases have area data but limited harvest records, making Tier 1 the primary operational tier.
Flow 1 — Latent Potential
- Lease area (hectares) from cadastral data
- Biophysical context: water temperature, salinity, trophic status
- Published unit ESV rates ($/kg N removed, $/tCO₂e, $/ha habitat)
- Activity Factor: fraction of lease under active cultivation
- DAF adjustment based on REDQS score
Flow 2 — Realized Contribution
- Verified harvest records (kg/yr) from state reporting
- Nitrogen content of harvested oyster tissue (2.3% by dry weight)
- Carbon content and shell carbonate accounting
- Habitat provision: SAV and EFH spatial overlay
- Higher REDQS scores unlock higher DAF values
In the current platform, all leases are calculated at Tier 1 (Latent Potential) due to the absence of verified harvest records in the public cadastral datasets for both Virginia and Maine. The satellite growth data integration for Maine (Kiffney et al. 2026) provides a pathway toward Tier 2 estimates by supplying a modelled yield proxy derived from Dynamic Energy Budget (DEB) theory.
Service Vectors
ESV Service Vectors
The framework quantifies four ecosystem service vectors. Each has a distinct unit value, data source, and biophysical basis. Unit values are drawn from peer-reviewed literature and government valuation studies, and applied consistently across both regions.
Nitrogen Removal
$20.00 / kg N removedOysters filter phytoplankton and particulate organic matter from the water column, incorporating nitrogen into shell and tissue. When harvested, this nitrogen is permanently removed from the watershed. The unit value is derived from the cost of equivalent nitrogen removal via wastewater treatment (Grabowski et al. 2021; Bricker et al. 2018).
Data inputs: Virginia: CBP DataHub TN loading data by growing area. Maine: DMR lease coordinates with regional TN loading estimates from Maine DEP coastal monitoring.
ESV_N = Acres × 38.1 kg/acre/yr × TN_adj × AF × $20/kg × DAF
Carbon Sequestration
$75.00 / tCO₂e sequesteredOyster shells are composed of approximately 44% calcium carbonate (CaCO₃). During calcification, oysters incorporate dissolved inorganic carbon into their shells, providing a long-term carbon sink when shells are not returned to the water. The 2.39× multiplier (Chen et al. 2025) accounts for the full carbonate system effect. The unit value is based on the social cost of carbon (US EPA 2023 revised estimate).
Data inputs: Shell weight estimated from biomass allometric relationships. Carbon fraction: 0.25 t/acre. CO₂e multiplier: 2.39.
ESV_C = Acres × 0.25 t/acre × 2.39 × AF × $75/t × DAF
Habitat Provision — Commercial Fisheries
$1,738 / ha habitat providedOyster reefs and lease structures provide three-dimensional biogenic habitat supporting juvenile fish and invertebrate populations, including commercially important species such as blue crab, striped bass, and flounder. The unit value is derived from habitat equivalency analysis (Grabowski et al. 2012). SAV and EFH multipliers are applied based on spatial proximity.
Data inputs: Lease area from cadastral polygons. Habitat quality modifier applied based on proximity to SAV beds and Essential Fish Habitat (EFH) designations from NOAA.
ESV_H_comm = Acres_ha × $1,738/ha × SAV_mult × EFH_mult × AF × DAF
Habitat Provision — Recreational Fisheries
$851 / ha habitat providedIn addition to commercial fisheries support, oyster habitat enhances recreational fishing opportunities, contributing to local tourism and quality of life. The unit value is derived from travel cost and contingent valuation studies of recreational fishing in Chesapeake Bay and Gulf of Maine (Bricker et al. 2018; Jin et al. 2012).
Data inputs: Same spatial basis as commercial habitat vector. Recreational value modifier applied based on proximity to public boat ramps and recreational fishing pressure data.
ESV_H_rec = Acres_ha × $851/ha × SAV_mult × EFH_mult × AF × DAF
Water filtration (Acres × 750k oysters × 50 gal/day) is reported as a co-benefit only — not included in the total ESV to avoid double-counting with nitrogen removal.
Data Quality
REDQS Scoring & Data Adequacy Factor
The REDQS (Reference Data Quality Score) system provides a standardised framework for assessing the confidence level of each ESV estimate. It is scored on a 1–5 scale and maps directly to a Data Adequacy Factor (DAF) that scales the raw ESV estimate to reflect data quality.
DAF = ((REDQS/5)² + REDQS/5) / 2
| REDQS | DAF | Confidence | Data Scenario |
|---|---|---|---|
| 1 | 0.12 | Very Low | Lease area only; no environmental context |
| 2 | 0.28 | Low | SST only (outside validated area) |
| 3 | 0.48 | Medium | SST + food proxy (validated area) / CBP segment data |
| 4 | 0.72 | High | Station within 2 km + verified data |
| 5 | 1.00 | Very High | On-farm sensors + Oceanfarmr harvest records |
In the current platform, Virginia leases are assigned REDQS 3 (CBP water quality data available, no satellite growth data). Maine leases within the Kiffney et al. (2026) validated area are assigned REDQS 3 (satellite DEB model validated). Maine leases outside the validated area are assigned REDQS 2 (SST climatology available, no food proxy or DEB model).
Region
Virginia — Chesapeake Bay
Virginia is the largest oyster-producing state in the US by lease area, with 4,635 active polygon leases covering 131,614 acres across Chesapeake Bay and its tributaries. Lease data is sourced from the Virginia Marine Resources Commission (MRC) KMZ dataset, providing polygon geometry, lease ID, status, and primary species for all registered leases.
Active Leases
4,635
Total Acreage
131,614 ac
ESV/yr (Tier 1)
$79.7M
N Removed
~3,150 t/yr
Water quality context for Virginia leases is derived from the Chesapeake Bay Program (CBP) DataHub, which provides total nitrogen (TN) loading estimates by tributary segment and growing area. Eight growing areas are defined: Lower Bay East, Lower Bay West, York River, Rappahannock River, Potomac River, Upper Bay, James River, and Eastern Shore. Each growing area receives a TN adjustment factor that scales the nitrogen removal ESV to reflect local nutrient loading conditions.
Region
Maine — Gulf of Maine
Maine has 158 active polygon leases covering 1,531 acres across the Gulf of Maine coast, from Casco Bay in the south to Washington County in the northeast. Lease data is sourced from the Maine Department of Marine Resources (DMR) ArcGIS REST service, providing polygon geometry, lease ID, status, species, and water classification for all registered leases.
Active Leases
158
Total Acreage
1,531 ac
ESV/yr (Tier 1)
$800k
Sat. Validated
101 leases
Maine's Gulf of Maine environment differs substantially from Chesapeake Bay: colder water temperatures (mean annual SST 8–12°C vs. 14–18°C in Virginia), shorter growing seasons (130–170 days above 10°C threshold vs. 220 days in Virginia), and lower nutrient loading due to the absence of large agricultural watersheds. These differences are captured in the Activity Factor and TN adjustment applied to Maine leases.
| Parameter | Virginia | Maine |
|---|---|---|
| Activity Factor | 0.603 (220 days/365) | 0.356–0.466 (130–170 days/365) |
| TN Adjustment | 0.90–1.40× (CBP segment) | 0.95–1.10× (SST-derived) |
| SAV Multiplier | 1.10× | 1.05× |
| EFH Multiplier | 1.05× | 1.05× |
| REDQS (default) | 3 | 2–3 |
| Satellite Data | Not applicable | Kiffney et al. 2026 (Casco Bay / Midcoast) |
| Time-to-Market | Not modelled | DEB model (validated area only) |
Satellite Integration
Satellite Growth Data — Maine
A key innovation in the Maine implementation is the integration of satellite-derived growth data from Kiffney et al. (2026), published in Aquaculture (Vol. 612). This study used Landsat 8/9 imagery at 30-metre resolution to derive two biophysical variables across the Maine coast: sea surface temperature (SST) and a food availability proxy (chlorophyll-a / particulate organic matter). These variables were used to parameterise a Dynamic Energy Budget (DEB) model for Crassostrea virginica, producing lease-level estimates of growth rate and time to market.
SST (Sea Surface Temp)
Derived from Landsat 8/9 thermal infrared band. 10-year climatology (2014–2024) at 30m resolution. Drives the temperature-dependent metabolic rate in the DEB model.
Food Proxy (Chl-a / POM)
Derived from Landsat 8/9 visible bands using empirical algorithms. Proxies phytoplankton and particulate organic matter availability — the primary food source for filter-feeding oysters.
Time to Market (DEB)
Estimated time (years) for an oyster to reach market size (75mm shell height) from seed deployment, derived from the DEB model parameterised with SST and food proxy data.
The satellite data is accessible via the Landsat 8/9 Viewer for Aquaculture Site Selection (Google Earth Engine app), developed by the University of Maine.
Standards Alignment
Reporting Standards Alignment
The framework is designed to support ESG disclosure aligned with three international standards. The table below summarises the mapping between framework outputs and specific disclosure requirements.
- Locate: Lease polygon coordinates and county / growing area groupings
- Evaluate: ESV per acre, REDQS score, and satellite biophysical context
- Assess: DAF-adjusted ESV totals and confidence intervals
- Prepare: Standardised output tables for TNFD disclosure annexes
- 304-1: Operational sites in or adjacent to protected areas (EFH, SAV overlays)
- 304-2: Significant impacts on biodiversity (habitat provision ESV vectors)
- 304-3: Habitats protected or restored (oyster reef area equivalent)
- 304-4: IUCN Red List species in areas affected by operations
- Ecosystem extent accounts: lease area by type and status
- Ecosystem condition accounts: REDQS score as condition indicator
- Ecosystem service flow accounts: annual ESV by service vector
- Monetary ecosystem asset accounts: capitalised ESV at 3% discount rate
Tool
ESV Calculator
The ESV Calculator allows users to estimate the ecosystem service value of an individual oyster lease using the Dual-Flow Framework. Enter the lease area, cultivation method, and water quality context to generate a Tier 1 ESV estimate across all four service vectors.
Disclaimer
ESV estimates generated by this calculator are indicative only and are derived from Tier 1 (area-based) calculations using published unit values. They do not constitute verified environmental credits, regulatory compliance values, or financial instruments. Values should not be used for investment decisions without independent verification. The NOAA-TDC Dual-Flow Framework is a research tool designed to support ESG reporting alignment with TNFD LEAP, GRI 304, and SEEA EA standards.
References
References
1. Bricker, S.B., Getchis, T.L., Chadwick, C.B., Rose, C.M., & Rose, J.M. (2016). Integration of ecosystem-services into a framework for oyster aquaculture site selection. Aquaculture, 453, 231–241.
2. Chen, C. et al. (2025). Carbon sequestration multiplier for bivalve aquaculture. PNAS.
3. Grabowski, J.H., Brumbaugh, R.D., Conrad, R.F., Keeler, A.G., Opaluch, J.J., Peterson, C.H., Piehler, M.F., Powers, S.P., & Smyth, A.R. (2012). Economic valuation of ecosystem services provided by oyster reefs. BioScience, 62(10), 900–909.
4. Grabowski, J.H. et al. (2021). Nitrogen removal rates in oyster aquaculture. Environmental Science & Technology, 55(1), 198–207.
5. Jin, D., Hoagland, P., & Morin, M. (2012). Linking economic and ecological models for a marine ecosystem. Ecological Economics, 78, 21–30.
6. Kiffney, T., Capistrant-Fossa, K., Swifte, A., Noji, T., Bricknell, I., & Hamlin, H. (2026). Using satellite remote sensing to assess sea surface temperature, oyster food availability, and estimated time to market at aquaculture lease sites in Maine, USA. Aquaculture, 612, 742293.
7. NOAA Chesapeake Bay Program DataHub. (2024). Total nitrogen loading by tributary segment. Retrieved from https://datahub.chesapeakebay.net
8. SEEA Ecosystem Accounting. (2021). System of Environmental-Economic Accounting — Ecosystem Accounting (SEEA EA). United Nations Statistics Division.
9. Taskforce on Nature-related Financial Disclosures. (2023). TNFD Recommendations and Guidance (v1.0). TNFD.
10. US EPA. (2023). Supplementary Material for the Regulatory Impact Analysis: Revised Social Cost of Carbon, Methane, and Nitrous Oxide. US Environmental Protection Agency.
11. Virginia Marine Resources Commission. (2024). Oyster Ground Lease Data. Retrieved from https://webapps.mrc.virginia.gov
12. Maine Department of Marine Resources. (2024). Aquaculture Lease and LPA Data. Retrieved from https://dmr-maine.opendata.arcgis.com