A desktop draft of the mine's EIA/ESG conformance — Ghana EPA (Act 490 / LI 1652) mapped against GISTM, IRMA, ICMM, IFC PS, ISSB S2, GRI 14 and TNFD, screened on Ghana-resolution spatial data — with an honest gap register of everything that still needs field data and a registered practitioner's sign-off.
This Snapshot screens Awaso Bauxite Mine (Ghana Bauxite Company Ltd, Bauxite) against Ghanaian regulatory requirements and international responsible-mining frameworks. It consolidates land, water, tailings/flood, air and closure screening into one audit-ready draft and a transparent gap register.
● Screening data: LIVE — SafeGround + FloodGuard across 9 concession points, queried 2026-06-14. Findings marked ○ seed are illustrative (no live engine for that aspect).
Readiness = share of framework requirements with desktop/GIS evidence already in place; the remainder need primary data, consultation or sign-off (see the gap register, §6). It is a drafting-progress measure, not a compliance score.
13 requirements need primary data or professional sign-off and are flagged, not assumed conformant. This is decision-support for a registered EIA practitioner — not a substitute for an EIS, field surveys, stakeholder consultation or audit.
| Mine | Awaso Bauxite Mine | Operator | Ghana Bauxite Company Ltd |
|---|---|---|---|
| Commodity | Bauxite | Status | Operating (since 1941) |
| Region / district | Western North Region / Bibiani-Anhwiaso-Bekwai | Nearest community | Awaso / Bibiani |
| Mine type | Open pit (hilltop terrace mining) | Processing | Crushing & screening only; ore railed to Takoradi for export (no on-site refining) |
⚑ Public-domain demonstration data only. Location approximate; concession boundary illustrative. No operator monitoring data used. For a live Snapshot, ingest the lease polygon, WRC permits and monitoring records.
| Indicator | Unit / screening benchmark |
|---|---|
| Forest & biodiversity | Natural-habitat / forest-reserve area cleared; net habitat change (IFC PS6 / TNFD) |
| Downstream water | Turbidity / TSS to receiving rivers; distance to water-supply intakes |
| Rehabilitation rate | ha disturbed vs ha progressively rehabilitated / reforested |
| Air quality | PM10 24-h vs Ghana EPA / WHO; haulage & rail-loading dust |
| Overburden / topsoil | Volumes stripped, stockpiled and reinstated; soil-profile reconstruction |
| GHG emissions | tCO₂e Scope 1/2/3 per t bauxite; energy & transport mix (ISSB S2) |
| Reclamation provision | Bond adequacy vs forest-restoration closure liability |
| Process chemistry | Crushing/screening only at mine — NO cyanide, NO mercury, NO wet TSF |
| Community grievances | Number, resolution time; farmland/forest-livelihood compensation |
| AMD / ML potential | Net acid generation (NAG) of overburden — typically low; confirm |
| Aspect | Status | Finding & evidence | Headline |
|---|---|---|---|
| Land & community context SafeGround · ● LIVE |
Gap HIGH | District: Bibiani-Anhwiaso-Bekwai-, Western North. Screened 9 points across the concession: 3/9 within/near a protected area; 0/9 near a catalogued contamination site. Land tenure, resettlement and grievance status require operator data. SafeGround /screen — protected-area & contamination layers ⚠ Gap: Forest-reserve status, Forestry Commission entry permits, biodiversity baseline and farmland-compensation records must be supplied by the operator. |
Bibiani-Anhwiaso-Bekwai-, Western North |
| Water resources & riparian SafeGround · ● LIVE |
Gap HIGH | Concession screened at 9 points. 1/9 within the riparian advisory buffer (nearest ~58 m); 0/9 near mapped wetland; 7/9 in a mapped flood-prone zone. Abstraction/discharge points need WRC permit cross-check. SafeGround /screen — river/wetland/flood layers ⚠ Gap: WRC abstraction/discharge permit numbers and turbidity/TSS monitoring data for downstream intakes required. |
Nearest watercourse ~58 m |
| Site drainage & downstream siltation FloodGuard · ● LIVE |
Needs primary data / sign-off HIGH | Live flood-susceptibility screen (national, 250 m grid) at 9 points: worst 'high', mean 0.40; 3/9 points high or above. Detailed drainage, erosion and downstream-receptor assessment still needs engineering input. FloodGuard /api/floodrisk/at — susceptibility grid; DEM-based downstream path screen; IDF extreme-rainfall context ⚠ Gap: Erosion & sediment-control plan, sediment-pond design and downstream turbidity monitoring required. |
Max susceptibility high (0.60) |
| Dust & air quality AirModule · ○ seed |
Partial MEDIUM | Lateritic dust corridors from terrace mining, crushing, haulage and rail loading toward the nearest communities identified; dust suppression coverage to be confirmed. Receptor proximity screen ⚠ Gap: Continuous PM10/PM2.5 monitoring records and a dust-management plan required. |
PM10 receptors within 1 km |
| Closure & forest restoration ReclamationModule · ○ seed |
Partial HIGH | Progressive rehabilitation footprint and a native-forest restoration strategy outlined for mined-out terraces — soil reconstruction and successional native planting rather than grass cover. Land-disturbance footprint; Native species suitability (GreenInfraPlants) ⚠ Gap: Audited closure cost estimate, reclamation bond adequacy and a forest-restoration success-criteria plan must be confirmed with EPA / Forestry Commission / Minerals Commission. |
Forest-restoration liability |
Desktop-derived status. Needs primary data / sign-off marks requirements that cannot be resolved without field data, stakeholder consultation or certification — see the gap register (§6).
| Clause | Requirement | Topic | Status | Evidence source |
|---|---|---|---|---|
| Reg. 1–3 | Registration & screening (Form EA1); mandatory EIA for mining (Schedule 2) | Procedure | Addressed (desktop) | EIA module |
| Reg. 12 | Scoping & Terms of Reference agreed with EPA | Procedure | Partial | EIA module |
| Reg. 13 | Environmental Impact Statement (EIS) content: baseline, impacts, mitigation | EIS content | Needs primary data / sign-off | All modules |
| Reg. 17 | Public hearing / stakeholder consultation record | Consultation | Needs primary data / sign-off | Stakeholder register |
| Reg. 23 | Environmental Management Plan (EMP) & monitoring commitments | Management | Partial | All modules |
| Reg. 24 | Annual Environmental Report & permit renewal | Compliance | Partial | Compliance dashboard |
| Clause | Requirement | Topic | Status | Evidence source |
|---|---|---|---|---|
| Reclamation | Reclamation plan & adequacy of reclamation security bond | Closure | Partial | Reclamation module |
| Clause | Requirement | Topic | Status | Evidence source |
|---|---|---|---|---|
| Topic I | Affected communities — knowledge base & engagement Not applicable to dry bauxite mining: no cyanide or mercury is used and there is no wet tailings storage facility (bauxite residue / red mud arises at the alumina refinery, not the mine), nor an artisanal gold-mining mercury interface. |
Tailings | Not applicable | — |
| Topic II | Integrated knowledge base — site characterisation, climate Not applicable to dry bauxite mining: no cyanide or mercury is used and there is no wet tailings storage facility (bauxite residue / red mud arises at the alumina refinery, not the mine), nor an artisanal gold-mining mercury interface. |
Tailings | Not applicable | — |
| Topic III | Design, construction, operation & monitoring of the TSF Not applicable to dry bauxite mining: no cyanide or mercury is used and there is no wet tailings storage facility (bauxite residue / red mud arises at the alumina refinery, not the mine), nor an artisanal gold-mining mercury interface. |
Tailings | Not applicable | — |
| Principle 4 | Consequence classification & dam-break/inundation assessment Not applicable to dry bauxite mining: no cyanide or mercury is used and there is no wet tailings storage facility (bauxite residue / red mud arises at the alumina refinery, not the mine), nor an artisanal gold-mining mercury interface. |
Tailings | Not applicable | — |
| Topic V | Emergency preparedness & response (EPRP) for downstream receptors Not applicable to dry bauxite mining: no cyanide or mercury is used and there is no wet tailings storage facility (bauxite residue / red mud arises at the alumina refinery, not the mine), nor an artisanal gold-mining mercury interface. |
Tailings | Not applicable | — |
| Topic VI | Governance — accountable executive, Independent Tailings Review Board Not applicable to dry bauxite mining: no cyanide or mercury is used and there is no wet tailings storage facility (bauxite residue / red mud arises at the alumina refinery, not the mine), nor an artisanal gold-mining mercury interface. |
Governance | Not applicable | — |
| Clause | Requirement | Topic | Status | Evidence source |
|---|---|---|---|---|
| Principle 3 | Human rights & free, prior and informed consent (FPIC) | Social | Needs primary data / sign-off | Stakeholder register |
| Principle 6 | Environmental performance — water, biodiversity, pollution | Environment | Gap | SafeGround / Air |
| Principle 6.3 | Cyanide management to ICMI Code Not applicable to dry bauxite mining: no cyanide or mercury is used and there is no wet tailings storage facility (bauxite residue / red mud arises at the alumina refinery, not the mine), nor an artisanal gold-mining mercury interface. |
Process | Not applicable | — |
| Principle 7 | Conservation of biodiversity & integrated land-use planning | Biodiversity | Partial | Reclamation module |
| Principle 9 | Social performance — resettlement, grievance mechanism | Social | Needs primary data / sign-off | Stakeholder register |
| Clause | Requirement | Topic | Status | Evidence source |
|---|---|---|---|---|
| 2.1 | Free, prior & informed consent | Social responsibility | Needs primary data / sign-off | Stakeholder register |
| 3.1 | Water management | Environmental responsibility | Gap | SafeGround |
| 3.2 | Air quality | Environmental responsibility | Partial | Air module |
| 3.5 | Tailings management | Environmental responsibility | Needs primary data / sign-off | FloodGuard |
| 3.6 | Cyanide management Not applicable to dry bauxite mining: no cyanide or mercury is used and there is no wet tailings storage facility (bauxite residue / red mud arises at the alumina refinery, not the mine), nor an artisanal gold-mining mercury interface. |
Environmental responsibility | Not applicable | — |
| 3.7 | Mercury management Not applicable to dry bauxite mining: no cyanide or mercury is used and there is no wet tailings storage facility (bauxite residue / red mud arises at the alumina refinery, not the mine), nor an artisanal gold-mining mercury interface. |
Environmental responsibility | Not applicable | — |
| 4.1 | Reclamation & closure planning for positive legacy | Positive legacy | Partial | Reclamation module |
| 4.2 | Biodiversity & ecosystem services | Positive legacy | Partial | Reclamation module |
| Clause | Requirement | Topic | Status | Evidence source |
|---|---|---|---|---|
| PS1 | Assessment & management of environmental & social risks | Management | Partial | All modules |
| PS3 | Resource efficiency & pollution prevention | Environment | Gap | SafeGround / Air |
| PS4 | Community health, safety & security (incl. dam safety) | Community | Needs primary data / sign-off | FloodGuard |
| PS5 | Land acquisition & involuntary resettlement | Social | Needs primary data / sign-off | SafeGround / Stakeholder |
| PS6 | Biodiversity conservation & living natural resources | Biodiversity | Partial | Reclamation module |
| Clause | Requirement | Topic | Status | Evidence source |
|---|---|---|---|---|
| Gov/Strat | Climate governance, strategy & transition plan | Climate | Gap | Operator disclosure |
| Metrics | Scope 1/2/3 GHG emissions | Climate | Needs primary data / sign-off | Energy inventory |
| Risk | Physical climate risk (extreme rainfall on TSF, water stress) | Climate | Needs primary data / sign-off | FloodGuard |
| Clause | Requirement | Topic | Status | Evidence source |
|---|---|---|---|---|
| 14.x | Tailings management disclosure | Sector | Needs primary data / sign-off | FloodGuard |
| 14.x | Water & effluents in mining | Sector | Gap | SafeGround |
| 14.x | Closure & rehabilitation | Sector | Partial | Reclamation module |
| 14.x | Artisanal & small-scale mining interface Not applicable to dry bauxite mining: no cyanide or mercury is used and there is no wet tailings storage facility (bauxite residue / red mud arises at the alumina refinery, not the mine), nor an artisanal gold-mining mercury interface. |
Sector | Not applicable | — |
| Clause | Requirement | Topic | Status | Evidence source |
|---|---|---|---|---|
| Locate | Interface with nature — habitats & water bodies in/near footprint | Nature | Gap | SafeGround |
| Evaluate | Dependencies & impacts on ecosystem services | Nature | Partial | Reclamation module |
| Assess | Nature-related risks & opportunities | Nature | Partial | Reclamation module |
| Prepare | Response & disclosure (net positive legacy target) | Nature | Gap | Operator disclosure |
| Clause | Requirement | Topic | Status | Evidence source |
|---|---|---|---|---|
| Forest entry | Forest-reserve entry permit, reclassification & compensatory planting | Forest | Needs primary data / sign-off | Forestry Commission |
| Clause | Requirement | Topic | Status | Evidence source |
|---|---|---|---|---|
| Critical habitat | Critical-habitat & forest-biodiversity assessment for hilltop bauxite | Biodiversity | Needs primary data / sign-off | Reclamation module |
| Clause | Requirement | Topic | Status | Evidence source |
|---|---|---|---|---|
| Downstream water | Protection of downstream water-supply intakes from siltation / turbidity | Water | Gap | SafeGround / WRC |
Bauxite caps forested hills, so the closure obligation is fundamentally a forest-restoration one: soil-profile reconstruction over mined-out terraces and re-establishment of native forest / agroforestry rather than mere grass cover. This is Resilicity's strongest positive-legacy case — a science-based reforestation and phytostabilisation plan (native Ghanaian species selection, substrate amelioration, successional planting) grounded in Aduse-Poku methodology, with measurable biodiversity and water-catchment co-benefits foregrounded as the reclamation & positive-legacy section.
| Species | Role in the reclamation plan |
|---|---|
| Terminalia ivorensis (Emire) | Fast native pioneer for forest-canopy re-establishment |
| Khaya ivorensis (African mahogany) | High-value native climax species; biodiversity |
| Milicia excelsa (Odum) | Native climax hardwood for long-term forest legacy |
| Albizia zygia | Leguminous nurse; soil-nitrogen amelioration |
| Chrysopogon zizanioides (vetiver) | Terrace & batter erosion control during establishment |
Order-of-magnitude screening estimate over ~200 ha of restored vegetation (~1,000 ha leaf area) using the Aduse-Poku deposition-velocity method (ScienceDirect 2024; Springer Urban Ecosystems 2025). Ambient from live FloodGuard regional data (Ababio 2025 (Western proxy)). Assumptions: Vd(NO₂)=0.0015 m/s, Vd(PM)=0.002 m/s, LAI=5.0, effective annual fraction=0.5, ambient NO₂=5.0 µg/m³, PM2.5=58.0 µg/m³ over 200 ha restored. Calibrate with site leaf-area index, species-specific Vd and measured ambient concentrations before reporting.
6 of 8 items are submission-blocking. A desktop Snapshot is an audit-ready draft; the items below require the operator, field teams and a registered EIA practitioner to close before any regulatory submission.
| # | Area | What is required | Owner | Severity |
|---|---|---|---|---|
| G01 | Land & community context | Forest-reserve status, Forestry Commission entry permits, biodiversity baseline and farmland-compensation records must be supplied by the operator. | Operator / consultant | BLOCKING |
| G02 | Water resources & riparian | WRC abstraction/discharge permit numbers and turbidity/TSS monitoring data for downstream intakes required. | Operator / consultant | BLOCKING |
| G03 | Site drainage & downstream siltation | Erosion & sediment-control plan, sediment-pond design and downstream turbidity monitoring required. | Operator / consultant | BLOCKING |
| G04 | Dust & air quality | Continuous PM10/PM2.5 monitoring records and a dust-management plan required. | Operator / consultant | Advisory |
| G05 | Closure & forest restoration | Audited closure cost estimate, reclamation bond adequacy and a forest-restoration success-criteria plan must be confirmed with EPA / Forestry Commission / Minerals Commission. | Operator / consultant | Advisory |
| G06 | Stakeholder consultation | Public hearing & FPIC records are legally required and must be conducted and documented. | Consultant / community | BLOCKING |
| G07 | Primary baseline surveys | Field ecology, hydrology, ambient air and social baseline surveys must be collected. | Field teams / labs | BLOCKING |
| G08 | Professional certification | EIS must be signed by an EPA-registered EIA practitioner; IRMA/GISTM require independent third-party audit. | Registered practitioner / auditor | BLOCKING |
Resilicity prepares a desktop EIA/ESG compliance snapshot like this one in hours, not weeks — across gold, lithium, bauxite and manganese, screened on Ghana data and structured for your EIA practitioner. Send us the concession and we'll screen it.