Law & Regulation
National Environmental Management Act 107 of 1998
The overarching statutory framework for cooperative environmental governance: environmental-management principles, the environmental-authorisation framework for listed/specified activities, duty of care, and compliance/enforcement architecture. Whether a project needs environmental authorisation depends on its activities, scale and location under the current Listing Notices; the EIA Regulations then prescribe the applicable procedural pathway.
Legal Significance
What This Instrument Does
Provides the overarching statutory framework for cooperative environmental governance: principles guiding organs of state, the legal basis for environmental assessment and authorisation of listed/specified activities, prohibition of unlawful commencement, and rectification, duty of care, pollution incidents, compliance monitoring and enforcement. Works through subordinate instruments and allocated competent authorities. Instrument boundary: does not grant land ownership, zoning, a water-use entitlement, a waste-management licence, building approval, electricity licence, mining right or procurement approval; environmental principles are not permits, and an environmental authorisation does not automatically cover every related activity, later design change or separate sector approval.
Why It Matters
Environmental authorisation can control site selection, layout, technology, mitigation, construction timing and operational conditions. Starting a listed activity without authorisation can expose the project and responsible persons to enforcement, delay, rectification and criminal risk; acquisition of an existing facility can carry legacy compliance and contamination exposure. Lenders typically require environmental due diligence, valid permits, compliance warranties and continuing covenants based on the actual authorised activity and conditions.
Key Provisions
- Section 2 — Environmental-management principles
Establishes principles including sustainable development, avoidance/minimisation of harm, participation and integrated decision-making. Practical consequence: project submissions should demonstrate how impacts are avoided, mitigated and managed; principles do not replace authorisation.
- Sections 11–16 — Environmental implementation and management plans
Coordinates environmental functions and planning across organs of state. Practical consequence: identify the competent authority rather than assume all decisions sit with DFFE.
- Section 23 — General objectives of integrated environmental management
Sets the aims of integrating environmental considerations into decisions affecting the environment. Practical consequence: evaluate alternatives and impacts early, before commercial design becomes irreversible.
- Section 24 — Environmental authorisations
Authorises identification of activities and areas requiring environmental assessment and approval and establishes the principal decision framework. Practical consequence: conduct a current Listing Notice screen before site commitment or construction mobilisation.
- Sections 24C–24D — Competent authority and coordination
Allocates decision authority and supports coordination of authorisations. Practical consequence: incorrect authority mapping can invalidate assumptions and delay the programme.
- Section 24E — Minimum conditions for authorisation
Requires decision-makers to comply with prescribed procedural and substantive conditions. Practical consequence: the application record must be sufficient for the authority to lawfully decide.
- Section 24F — Prohibition on unlawful commencement
Prohibits commencement of a listed or specified activity without required environmental authorisation. Practical consequence: define "commencement" conservatively and make authorisation a genuine pre-start control.
- Section 24G — Rectification of unlawful commencement
Provides a statutory application route concerning unlawfully commenced listed activities, subject to investigation, payment and authority discretion. Practical consequence: rectification is not advance permission — price outcome and enforcement risk in acquisition diligence.
- Section 24N — Environmental management programme
Regulates environmental-management programme content and implementation where required. Practical consequence: flow EMP obligations into EPC/O&M scopes, monitoring and lender reporting.
- Section 28 — Duty of care and remediation
Requires persons causing, having caused or controlling significant pollution or degradation to take reasonable measures to prevent, minimise and remedy it. Practical consequence: liability analysis extends beyond permit ownership.
- Section 30 — Control of emergency incidents
Requires reporting and response to specified unexpected pollution incidents. Practical consequence: emergency plans must include statutory notification, containment, remediation and evidence preservation.
- Sections 31A–31L — Environmental management inspectors
Establishes inspectors and powers for monitoring, inspection and enforcement. Practical consequence: maintain accessible permit, monitoring and incident records.
- Section 43 — Appeals
Provides a statutory appeal framework for specified environmental decisions. Practical consequence: account for appeal periods in financing and construction dates.
- Sections 49A–49B — Offences and penalties
Identifies serious contraventions and potential liability. Practical consequence: environmental obligations require board-level controls where exposure is material.
InfraLex Relevance
The framework environmental layer in South African project development; the EIA Regulations implement its assessment process while Listing Notices determine project-specific triggers, and water/waste regimes remain separate approval systems.
Legal Framework Position
- Environmental / PermittingPrimary / Framework Instrument
Instrument Overview
- Official Citation
- 107 of 1998; Government Gazette 19519, 27 November 1998
- Instrument Type
- Law / Act
- Source Language
- English
- Enactment Date
- 27 November 1998
- Last Verified
- 6 September 2026