Companion to TG-3.16 Quality Assurance and Quality Control of Ocean Asset Accounts, Section 3.8. The example is synthetic, and every table is generated by one script from one set of inputs. Tables marked "as submitted" contain the nine seeded errors (E1 to E9) and are not models. The QC log is also available as CSV.
GOAP Secretariat. Consultation draft, licensed CC BY-NC 4.0.
| Parameter | As submitted | Corrected | Source or basis |
|---|---|---|---|
| Accounting area (EAA) | 1,200 km² | 1,200 km² | Fixed; area computed in EPSG:6933 (WGS 84 / NSIDC EASE-Grid 2.0 Global, equal-area) |
| Discount rate, horizon | 4%, 30 years | 4%, 30 years | SOP C6 default; annuity factor 17.292; grid 2/4/7% |
| Carbon price | USD 185 per tCO₂e (social cost of carbon) | USD 30 per tCO₂e (exchange value) | National emissions-trading scheme, 2025 mean auction price (synthetic) |
| Carbon conversion | 44/12 tCO₂e per tC | 44/12 tCO₂e per tC | SOP C8 |
| Resource rent for the period | 3,200 | 3,200 | Output 13,440 − IC 5,100 − CoE 3,200 − CFC 900 − normal return 1,040 |
| Unit rent, opening → closing | 0.45 → 0.49 | 0.45 → 0.49 | USD thousand per tonne of catch |
| Live-weight factor | 1.25 | 1.25 | National conversion-factor table, gutted to live weight, one factor for this species and form |
| Condition-to-service form | Linear (screening) | Linear (screening) | Labelled as such; likely bias: understates loss near a threshold |
| Trajectory | Held at closing condition | Held at closing condition | Flows held at the closing condition. Two observations do not establish a trend; TG-4.8 asks for a record of at least ten years before a trend is claimed |
| Horizon | Finite | Finite | Finite 30-year horizon: the management plan that sustains the flows renews every ten years and renewal beyond 2055 is not assured (TG-3.1 Section 3.5.3) |
| Accounting entry | Mangrove | Seagrass | Aquaculture ponds | Subtidal sediment | Shelf waters | Total |
|---|---|---|---|---|---|---|
| Opening extent | 60.0 | 25.0 | 15.0 | 300.0 | 800.0 | 1,200.0 |
| Managed expansion | 0.0 | 0.0 | 0.0 | 0.0 | 0.0 | 0.0 |
| Unmanaged expansion | 0.0 | 0.0 | 0.0 | 0.0 | 0.0 | 0.0 |
| Managed reduction | -0.4 | 0.0 | 0.0 | 0.0 | 0.0 | -0.4 |
| Unmanaged reduction | 0.0 | 0.0 | 0.0 | 0.0 | 0.0 | 0.0 |
| Conversions from other types | 0.0 | 0.0 | 0.0 | 0.6 | 0.0 | 0.6 |
| Conversions to other types | 0.0 | -0.6 | 0.0 | 0.0 | 0.0 | -0.6 |
| Net reclassification | 0.0 | -0.6 | 0.0 | 0.6 | 0.0 | 0.0 |
| Closing extent | 59.6 | 24.4 | 15.0 | 300.6 | 800.0 | 1,199.6 |
| Opening type ↓ / closing type → | Mangrove | Seagrass | Aquaculture ponds | Subtidal sediment | Shelf waters | Opening (row sum) |
|---|---|---|---|---|---|---|
| Mangrove | 59.6 | 0.0 | 0.4 | 0.0 | 0.0 | 60.0 |
| Seagrass | 0.0 | 24.1 | 0.0 | 0.9 | 0.0 | 25.0 |
| Aquaculture ponds | 0.0 | 0.0 | 15.0 | 0.0 | 0.0 | 15.0 |
| Subtidal sediment | 0.0 | 0.3 | 0.0 | 299.7 | 0.0 | 300.0 |
| Shelf waters | 0.0 | 0.0 | 0.0 | 0.0 | 800.0 | 800.0 |
| Closing (column sum) | 59.6 | 24.4 | 15.4 | 300.6 | 800.0 | 1,200.0 |
| ECT class | Variable | Unit | Polarity | L | U | Opening | Closing |
|---|---|---|---|---|---|---|---|
| A1 Physical state | Surface elevation gain less relative sea-level rise | mm/yr | Normal | -4 | 4 | 1.6 | 1.2 |
| A2 Chemical state | Porewater salinity | ppt | Inverse | 60 | 30 | 39 | 41 |
| B1 Compositional state | True-mangrove species per plot | count | Normal | 1 | 9 | 7 | 7 |
| B2 Structural state | Canopy cover | % | Normal | 20 | 90 | 76 | 72 |
| B3 Functional state | Seedling recruitment | per m² | Normal | 0 | 5 | 3.4 | 3.1 |
| C1 Seascape | Share of mangrove in patches over 10 ha | % | Normal | 40 | 100 | 85 | 83 |
| ECT class | Opening indicator | Closing indicator | Change | Flag |
|---|---|---|---|---|
| A1 Physical state | 0.700 | 0.650 | -0.050 | [B] |
| A2 Chemical state | 0.700 | 0.633 | -0.067 | [A] |
| B1 Compositional state | 0.750 | 0.750 | 0.000 | [A] |
| B2 Structural state | 0.800 | 0.743 | -0.057 | [A] |
| B3 Functional state | 0.680 | 0.620 | -0.060 | [B] |
| C1 Seascape | 0.750 | 0.717 | -0.033 | [A] |
| Aggregation rule | Opening | Closing | Change |
|---|---|---|---|
| Arithmetic mean, equal weights (published) | 0.730 | 0.685 [B] | -0.045 |
| Geometric mean (sensitivity) | 0.729 | 0.683 | -0.045 |
| One-out-all-out (sensitivity) | 0.680 | 0.620 | -0.060 |
| Entry | Tonnes (live weight) | Source |
|---|---|---|
| Opening stock (total biomass) | 36,000 | Assessment |
| Growth in stock | 9,000 | Assessment production model |
| Gross catch (landings plus discards) | -7,000 | Landings 6,400 + discards 600 |
| Normal natural losses | -2,786 | Baranov: (M/Z) B₀ (1 − e^−Z) |
| Catastrophic losses | -500 | Hypoxia event, documented trigger |
| Reappraisal (assessed less identity closing) | -414 | Residual shown, not absorbed |
| Closing stock (total biomass) | 34,300 | Assessment |
| Memorandum: sustainable yield at current biomass | 6,200 | Assessment, on SSB |
| Memorandum: depletion, max(0, catch − SY) | 800 | Derived |
| Memorandum: stock status B/B_MSY, opening → closing | 2.00 → 1.91 | On total biomass |
| Cross-check: Baranov predicted catch | 6,810 | (F/Z) B₀ (1 − e^−Z); gap 2.7% |
| Accounting entry | Mangrove | Seagrass | Aquaculture ponds | Total |
|---|---|---|---|---|
| Opening value | 132,859 | 22,587 | 0 | 155,446 |
| Ecosystem enhancement | 0 | 0 | 0 | 0 |
| Ecosystem degradation | -5,066 | .. | .. | -5,066 |
| Ecosystem conversions (additions) | 0 | 271 | 0 | 271 |
| Ecosystem conversions (reductions) | -886 | -8,131 | 0 | -9,017 |
| Catastrophic losses | 0 | 0 | 0 | 0 |
| Reappraisals | 0 | 0 | 0 | 0 |
| Revaluation | 0 | 0 | 0 | 0 |
| Closing value | 126,907 | 14,727 | 0 | 141,634 |
Subtidal sediment and Shelf waters: not valued (".."), so not shown. Aquaculture ponds: a confirmed zero, not a gap.
| Entry | Tonnes | USD thousand |
|---|---|---|
| Opening value | 36,000 | 49,023 |
| Growth in stock | 9,000 | 12,798 |
| Gross catch | -7,000 | -10,665 |
| Normal natural losses | -2,786 | -3,961 |
| Catastrophic losses | -500 | -711 |
| Reappraisal | -414 | -589 |
| Revaluation | 4,944 | |
| Closing value | 34,300 | 50,839 |
| Memorandum: depletion at the mid-period price | 800 | 1,138 |
| Memorandum: volume change at opening prices | -1,700 | -2,315 |
| Asset | Opening value | Closing value |
|---|---|---|
| Mangrove | 132,859 | 126,907 |
| Seagrass | 22,587 | 14,727 |
| Aquaculture ponds | 0 | 0 |
| Ecosystem assets, total | 204,469 | 192,472 |
| Memorandum: demersal stock (SEEA CF, stand-alone; not added) | 49,023 | 50,839 |
| Check | Cell | Finding |
|---|---|---|
| AQ-ID3 | WE-2 total closing | Closing total 1,199.6 km² against an EAA of 1,200.0 km² |
| AQ-ID4 | WE-2 mangrove reductions | 0.4 km² leaves mangrove with no destination type and no change to the EAA boundary |
| AQ-ID5 | WE-2 mangrove conversions to | Account records 0.0 km²; matrix off-diagonals give 0.4 km² |
| AQ-ID5 | WE-2 seagrass conversions to | Account records 0.6 km²; matrix off-diagonals give 0.9 km² |
| AQ-ID5 | WE-2 seagrass conversions from | Account records 0.0 km²; matrix off-diagonals give 0.3 km² |
| AQ-ID5 | WE-3 ponds column | Column margin 15.4 km² against closing extent 15.0 km² |
| AQ-ID5 | WE-2 ponds conversions from | Account records 0.0 km²; matrix off-diagonals give 0.4 km² |
| AQ-ID5 | WE-2 sediment conversions to | Account records 0.0 km²; matrix off-diagonals give 0.3 km² |
| AQ-ID5 | WE-2 sediment conversions from | Account records 0.6 km²; matrix off-diagonals give 0.9 km² |
| AQ-ID6 | WE-6c total opening | Total exceeds the ecosystem types by 49,023, the stand-alone SEEA CF fish-stock value |
| AQ-ID6 | WE-6c total closing | Total exceeds the ecosystem types by 50,839, the stand-alone SEEA CF fish-stock value |
| AQ-UN1 | WE-6a seagrass conversions (reductions) | Implied 9,035 per km² against an opening unit value of 903 per km²: about 10 times |
| AQ-UN4 | text N1 | Text says 0.667; recomputed 0.033 |
| AQ-PM1 | WE-6b catch | Entry values 7,500 t; the physical account records 7,000 t |
| AQ-PM4 | WE-6a mangrove degradation | Entry -5,066; index decline × PV of affected services gives -3,579 |
| AQ-VA2 | WE-6a mangrove opening | Value implies a condition factor of 0.533; the index is 0.730 (the index squared) |
| AQ-VA2 | WE-6a mangrove closing | Value implies a condition factor of 0.470; the index is 0.685 (the index squared) |
| AQ-VA3 | WE-6a mangrove degradation | Largest service (carbon) is 60% of annual flow value, not over 70% |
| AQ-VA6 | WE-1 carbon price | Carbon priced on an SCC basis (USD 185 per tCO₂e); account cells hold exchange values |
| AQ-FS1 | WE-5 B/BMSY | Ratio 1.91 computed on total biomass; on SSB it is 0.78 |
| AQ-EV2 | WE-6a seagrass conversions (reductions) | Entry -8,131; 0.9 km² × 903.5 gives -813 |
| Accounting entry | Mangrove | Seagrass | Aquaculture ponds | Subtidal sediment | Shelf waters | Total |
|---|---|---|---|---|---|---|
| Opening extent | 60.0 [A] | 25.0 [B] | 15.0 [A] | 300.0 [B] | 800.0 [A] | 1,200.0 [B] |
| Managed expansion | 0.0 | 0.0 | 0.0 | 0.0 | 0.0 | 0.0 |
| Unmanaged expansion | 0.0 | 0.0 | 0.0 | 0.0 | 0.0 | 0.0 |
| Managed reduction | 0.0 | 0.0 | 0.0 | 0.0 | 0.0 | 0.0 |
| Unmanaged reduction | 0.0 | 0.0 | 0.0 | 0.0 | 0.0 | 0.0 |
| Conversions from other types | 0.0 | 0.3 | 0.4 | 0.9 | 0.0 | 1.6 |
| Conversions to other types | -0.4 | -0.9 | 0.0 | -0.3 | 0.0 | -1.6 |
| Net reclassification | -0.4 | -0.6 | 0.4 | 0.6 | 0.0 | 0.0 |
| Closing extent | 59.6 [A] | 24.4 [B] | 15.4 [A] | 300.6 [B] | 800.0 [A] | 1,200.0 [B] |
| Entry | Tonnes (live weight) | Source |
|---|---|---|
| Opening stock (total biomass) | 36,000 [B] | Assessment |
| Growth in stock | 9,000 [B·E] | Assessment production model |
| Gross catch (landings plus discards) | -7,000 [B] | Landings 6,400 + discards 600 |
| Normal natural losses | -2,786 [B·E] | Baranov: (M/Z) B₀ (1 − e^−Z) |
| Catastrophic losses | -500 [C] | Hypoxia event, documented trigger |
| Reappraisal (assessed less identity closing) | -414 [B] | Residual shown, not absorbed |
| Closing stock (total biomass) | 34,300 [B·E] | Assessment |
| Memorandum: sustainable yield at current biomass | 6,200 [B·E] | Assessment, on SSB |
| Memorandum: depletion, max(0, catch − SY) | 800 [B·E] | Derived |
| Memorandum: stock status B/B_MSY, opening → closing | 0.82 → 0.78 | On SSB |
| Cross-check: Baranov predicted catch | 6,810 | (F/Z) B₀ (1 − e^−Z); gap 2.7% |
| Accounting entry | Mangrove | Seagrass | Aquaculture ponds | Total |
|---|---|---|---|---|
| Opening value | 73,628 [C·E] | 14,529 [C·E] | 0 [A] | 88,157 [C·E] |
| Ecosystem enhancement | 0 | 0 | 0 | 0 |
| Ecosystem degradation | -3,579 | .. | .. | -3,579 |
| Ecosystem conversions (additions) | 0 | 174 | 0 | 174 |
| Ecosystem conversions (reductions) | -491 | -523 | 0 | -1,014 |
| Catastrophic losses | 0 | 0 | 0 | 0 |
| Reappraisals | 0 | 0 | 0 | 0 |
| Revaluation | 0 | 0 | 0 | 0 |
| Closing value | 69,558 [C·E] | 14,180 [C·E] | 0 [A] | 83,738 [C·E] |
Subtidal sediment and Shelf waters: not valued (".."), so not shown. Aquaculture ponds: a confirmed zero, not a gap.
| Entry | Tonnes | USD thousand |
|---|---|---|
| Opening value | 36,000 | 49,023 [C·E] |
| Growth in stock | 9,000 | 12,798 |
| Gross catch | -7,000 | -9,954 |
| Normal natural losses | -2,786 | -3,961 |
| Catastrophic losses | -500 | -711 |
| Reappraisal | -414 | -589 |
| Revaluation | 4,233 | |
| Closing value | 34,300 | 50,839 [C·E] |
| Memorandum: depletion at the mid-period price | 800 | 1,138 [C·E] |
| Memorandum: volume change at opening prices | -1,700 | -2,315 |
| Asset | Opening value | Closing value |
|---|---|---|
| Mangrove | 73,628 [C·E] | 69,558 [C·E] |
| Seagrass | 14,529 [C·E] | 14,180 [C·E] |
| Aquaculture ponds | 0 [A] | 0 [A] |
| Ecosystem assets, total | 88,157 [C·E] | 83,738 [C·E] |
| Memorandum: demersal stock (SEEA CF, stand-alone; not added) | 49,023 [C·E] | 50,839 [C·E] |
| ID | Reconcile or verify | Account | Comparator | Difference | Result |
|---|---|---|---|---|---|
| AQ-RC1 | Extraction = PSUT natural input (t) | 7,000 | 7,000 | 0 | Pass |
| AQ-RC2 | Depletion = NDP deduction (USD thousand) | 1,138 | 1,138 | 0 | Pass |
| AQ-RC6 | Change-matrix margins = extent (run as AQ-ID5) | 1,200.0 | 1,200.0 | 0.0 | Pass |
| AQ-VF1 | Mangrove extent vs global product (km²) | 59.6 | 57.8 | 3.1% | Pass (under 15%) |
| AQ-VF2 | Closing stock vs independent assessment (t) | 34,300 | 33,500 | 2.4% | Pass (under 15%) |
| AQ-VF2 | Landings vs FishStatJ (t) | 6,400 | 6,380 | 0.3% | Pass (under 15%) |
| Map class | Points | User accuracy | Producer accuracy | Mapped (km²) | Area-adjusted (km²) | 95% CI (km²) |
|---|---|---|---|---|---|---|
| Mangrove | 100 | 0.950 | 0.949 | 59.6 | 59.6 | 56.5 to 62.8 |
| Aquaculture ponds | 60 | 0.933 | 0.905 | 15.4 | 15.9 | 13.9 to 17.9 |
| Other | 80 | 0.888 | 0.906 | 25.0 | 24.5 | 21.7 to 27.2 |
| Asset (closing value, USD thousand) | Method | Central (MC: median) | 95% range | Relative half-width | Grade |
|---|---|---|---|---|---|
| Mangrove | Monte Carlo, 10,000 draws | 66,345 | 39,134 to 124,469 | 64% | C |
| Seagrass | Analytic (first order) | 14,180 | ± 74% | 74% | C |
| Demersal stock | Analytic (first order) | 50,839 | ± 44% | 44% | C |
| Discount rate | Mangrove closing value | Demersal stock closing value |
|---|---|---|
| 2% | 90,090 | 65,846 |
| 4% | 69,558 | 50,839 |
| 7% | 49,916 | 36,483 |