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Environmental Law

Environmental Compensation in Development Projects: Obligations and Costs

March 15, 2026

Environmental Compensation in Development Projects: Obligations and Costs

Environmental compensation constitutes one of the most underestimated line items in the financial structuring of real estate, tourism, and industrial development projects in Mexico. Its activation does not depend on the developer’s will but rather on the occurrence of specific normative assumptions, and its quantification can substantially modify the economic viability of a project. Ignoring it during the due diligence stage has consequences ranging from costly conditions to authorization denial.

Applicable Regulatory Framework

The environmental compensation regime in Mexico rests on three fundamental instruments. The General Law on Ecological Balance and Environmental Protection (LGEEPA), published in the Federal Official Gazette on January 28, 1988 and with amendments in effect as of January 2022, establishes in its article 30 that the Environmental Impact Statement (MIA) must identify, describe, and evaluate the significant effects of the project on the environment, and that the Secretariat of Environment and Natural Resources (SEMARNAT) may condition authorization on the execution of mitigation or compensation measures. SEMARNAT’s authority to deny authorization when impacts are irreversible or cannot be adequately compensated is based on article 35, third paragraph, subsection III of the LGEEPA, pursuant to which the authority must deny authorization when, despite the proposed measures, the negative effects on the environment are irreversible or the residual impact exceeds environmental acceptability thresholds. This is the provision applicable to the denial authority; it should not be confused with article 35 bis 1, whose purpose is to regulate the content requirements of the Environmental Impact Statement for works in wetlands under federal jurisdiction.

The General Law on Sustainable Forest Development (LGDFS), in its text in effect with amendments published in the DOF on April 13, 2020, regulates Change of Land Use in Forest Lands (CUSTF) through specific provisions whose proper identification is relevant for project planning. Article 93 requires express SEMARNAT authorization for any change of land use in forest lands, with no minimum surface area exception. Article 97 establishes the obligation of environmental compensation, specifically deposit to the Mexican Forest Fund or the execution of equivalent reforestation or restoration actions on surfaces of equal or greater extent and environmental quality than the affected area, as well as the criteria for determining the magnitude of compensation. The Technical Justification Study (ETJ) required as a procedural condition for the CUSTF request is regulated in accordance with the regulatory provisions applicable to article 93 and the technical guidelines issued by SEMARNAT, which establish its minimum content regarding vegetation inventory, environmental services analysis, and compensation proposal. Reference to a generic range of articles 93 to 101 is insufficient to guide technical planning; the developer’s operational obligations are concentrated in articles 93 and 97.

At the state level, the Environmental Code of the State of Quintana Roo, with amendments in effect as of 2023, introduces complementary compensation obligations for projects subject to state environmental impact assessment, particularly when coastal wetlands, mangroves, or medium evergreen forest ecosystems are affected.

When the Compensation Obligation is Activated

Environmental compensation does not operate automatically upon any territorial intervention. Its activation depends on three cumulative thresholds: the classification of the land as forest, of preferentially forest aptitude, or as an area of relevant vegetation in accordance with the official inventory; the magnitude of the residual impact, that is, the one that subsists after the application of prevention and mitigation measures; and the determination of the authority in the MIA resolution or in the CUSTF resolution.

In the Riviera Maya, given the high density of mangrove vegetation, subperennial medium forest, and coastal dune systems, the majority of medium and large-scale development projects activate compensation. The Mexican Official Standard NOM-022-SEMARNAT-2003, which establishes the specifications for preservation, conservation, sustainable use, and restoration of coastal wetlands in mangrove zones, imposes particularly severe restrictions: its normative point 4.3 prohibits filling, desiccation, or any work that affects the hydrological connectivity of the mangrove, and its breach is not subject to compensation but rather to mandatory restoration and penalty.

Procedural Timelines of CUSTF and Its Impact on Project Critical Path

An element frequently omitted from financial planning is the resolution timeline for the CUSTF, which constitutes a critical variable for the project closing schedule and carry cost. In accordance with the LGDFS and its regulations, SEMARNAT has a formal period of sixty business days to issue a resolution on a CUSTF request from the submission of complete documentation. However, in practice, this timeline is materially extended for various reasons: requests for additional information that suspend the computation, technical objections regarding the content of the Technical Justification Study, or the need for inter-institutional consultations when the property is located in areas of concurrent jurisdictional authority.

The effective timeline for obtaining a CUSTF resolution in projects of moderate complexity in Quintana Roo frequently ranges between five and twelve months from the submission of the request, with cases of greater complexity exceeding that range. This operational reality has two direct financial consequences: it prolongs the period of capital immobilization invested in the acquisition of the property and generates uncertainty regarding the closing conditions of financing instruments that require the obtaining of environmental authorizations as a precedent condition.

Additionally, when the project requires both CUSTF resolution and MIA authorization, both proceedings may be conducted concurrently or sequentially depending on the proponent’s strategy. Concurrent processing reduces total time but increases the risk of inconsistencies between the technical assumptions of both procedures; sequential processing offers greater consistency but lengthens the critical path. This decision must be made at the project structuring stage, with full consideration of its effects on the disbursement schedule and financing conditions.

Quantification of Compensation Cost

The compensation cost varies depending on the mechanism chosen or imposed by the administrative resolution. Under the Mexican Forest Fund scheme provided for in Article 97 of the LGDFS, the amount is calculated in accordance with value tables for environmental services of the affected ecosystem, periodically updated by SEMARNAT through an agreement published in the DOF. SEMARNAT publishes and updates these environmental services valuation tables for different types of vegetation and regions of the country; the specific values applicable to the semi-evergreen medium forest in Quintana Roo are established in the corresponding agreements of the General Directorate of Forest Management and Soils. Since these values are updated periodically, the developer must directly consult the current tables on the CONAFOR portal (www.conafor.gob.mx) and verify the most recent update agreement published in the DOF at the time of preparing the project financial model. As an informational reference, environmental service values for medium forest ecosystems in the southeastern region have historically recorded ranges that can exceed one hundred thousand pesos per hectare in certain valuation categories, although the final amount depends on the specific classification of the ecosystem, the forest aptitude zone, and the agreement in force at the time of resolution. For medium-scale projects in Quintana Roo involving several dozen forest hectares, the aggregate of compensatory obligations can represent several millions of pesos, constituting a cost item that must be projected with precision before the execution of any binding instrument.

When compensation is executed through direct actions, the developer must accredit the acquisition or commitment of an equivalent surface area, the execution of reforestation work with native species, and monitoring during a minimum period determined by the resolution. This scheme may be less costly in cash but implies greater operational complexity and non-compliance risks.

Impact on Project Viability

Viability analysis must incorporate environmental compensation from the site evaluation stage, not as a contingency but as a certain conditioned cost. The most frequent errors in projects that reach litigation are three: the omission of the CUSTF under the mistaken belief that the clearing of secondary vegetation does not require authorization; the underestimation of the forest surface within the project polygon due to deficiencies in the vegetation study; and the absence of financial reserve to cover the compensation cost when the MIA resolution proves more restrictive than projected.

The Collegiate Courts of the XXVII Circuit with headquarters in Cancún have developed a consistent interpretive line regarding amparo actions against environmental impact resolutions, to the effect that authorization in matters of environmental impact constitutes a discretionary act of the environmental authority subject to the principles of precaution and environmental non-regression, and that the burden of demonstrating the sufficiency of the proposed compensatory measures falls upon the project proponent. It is important to clarify that this characterization reflects the general interpretive tendency of said circuit, identifiable in the matters resolved in environmental matters by that jurisdiction, without having located and verified at the time of preparation of this article isolated theses or jurisprudence published in the Semanario Judicial de la Federación with a specific registration number that exactly capture this formulation. The reader interested in invoking this criterion in a specific proceeding must verify the existence and text of applicable theses in the SJF search tool (sjf.scjn.gob.mx) before citing them as formal precedent.

In the same sense, the First Chamber of the SCJN has held, in line with the constitutional criterion derived from the interpretation of article 4° of the Constitution regarding the right to a healthy environment, that this right operates as a proportional limit to the rights of property and free enterprise, and that environmental compensation measures are constitutionally valid even when they imply significant economic burdens for individuals, provided that they are proportional to the impact generated and are duly grounded in technical evidence. This position is consistent with the First Chamber’s jurisprudential line on third-generation fundamental rights, although the developer who needs to invoke a specific thesis of the First Chamber before a court must verify the registration number and exact subject matter of the thesis in the Semanario Judicial de la Federación, given that the foregoing formulation reflects the general tendency and does not constitute a textual citation of a thesis published with verified registration.

Overlay of Protected Natural Areas

A factor that frequently elevates substantially the complexity and cost of the authorization process in the Riviera Maya is the superposition of the property or its area of influence with a Protected Natural Area (ANP) of federal competence. The region has ANPs of significant relevance, among them the Sian Ka’an Biosphere Reserve, the Cozumel Reefs National Park, the Tulum National Park and other flora and fauna protection areas with current federal declarations. When a project is located within the polygon of an ANP or in its buffer zone, the applicable regulatory framework expands materially.

Pursuant to articles 46 through 51 of the LGEEPA, ANPs are governed by their creation decrees and by their management programs, which establish the activities permitted, conditioned and prohibited in each zone of the protected area. The authorization of a project in this context is not processed solely under the general environmental impact regime of article 28 of the LGEEPA, but rather requires an analysis of compatibility with the management program of the ANP, processed before the Directorate of the corresponding Protected Natural Area under the coordination of the National Commission of Protected Natural Areas (CONANP). This process constitutes an authorization independent of the EIA, with its own legal basis and its own evaluation logic.

The practical consequences for the developer are significant in several respects. First, the compensation conditions in projects within or adjacent to ANPs are typically more onerous than those imposed on projects in forest areas without special protection, insofar as the ecosystems involved receive a differentiated valuation by reason of their protection status. Second, the term for obtaining both authorizations is prolonged, given that compatibility with the ANP’s management program must be resolved before or in parallel with the evaluation of the EIA. Third, a finding of incompatibility by CONANP may determine the total inviability of the project regardless of the outcome of the EIA proceeding. The evaluation of the ANP status of the property and its area of influence is, therefore, a matter of first order in any environmental due diligence process in the Riviera Maya.

Criminal Liability: Scope and Correct Delimitation

The criminal exposure of the developer in environmental matters does not derive directly from non-compliance with a compensation condition imposed in the EIA resolution, but rather from the underlying material acts that configure autonomous criminal offenses in the Federal Criminal Code. This distinction is relevant to correctly structure the risk assessment.

Article 418 of the Federal Penal Code typifies the change of land use in forest lands without authorization from SEMARNAT, as well as the carrying out of clearing or cleaning in forest lands in contravention of applicable legislation. Consequently, a developer who initiates clearing works or modification of forest vegetation cover without having previously obtained the CUSTF resolution incurs the assumption of article 418, regardless of whether or not it has MIA authorization. The obtaining of the MIA does not remedy the absence of CUSTF authorization for criminal purposes.

Article 420 of the Federal Penal Code typifies various conducts that affect wildlife, ecosystems and species in special protection category. Its application in the context of development projects is activated when the works affect the habitat of protected species or generate damage to fragile ecosystems, including coral reefs, coastal wetlands and underground cave systems (cenotes) that characterize the geography of Quintana Roo’s subsoil.

The situation of greatest criminal risk is configured when the developer proceeds with material works without having the required authorizations, or when executing works in violation of the conditions of the resolution in such a way that the acts carried out constitute, in themselves, conducts typified in articles 418 or 420. The non-compliance with an administrative condition of a compensatory nature does not generate criminal responsibility by itself, but can be evidence of the commission of one of the aforementioned criminal types if it is accompanied by material acts of destruction or unauthorized affectation.

Post-Resolution Compliance

The obtaining of MIA authorization and the CUSTF resolution does not exhaust the developer’s obligations in environmental matters. The MIA resolution invariably incorporates a set of conditions whose compliance is enforceable throughout the entire project execution phase, and whose non-observance generates administrative, financial and reputational consequences of the first order.

The most frequent conditions in projects in Quintana Roo include the submission of compliance reports of compensation measures within determined deadlines, the carrying out of verification visits by the authority or a certified third party, the maintenance of photographic and technical records of reforestation or restoration actions, and the submission of vegetation monitoring reports on the compensation properties during the periods established in the resolution. Non-compliance with any of these conditions may motivate the opening of an administrative inspection procedure by the Federal Environmental Protection Agency (PROFEPA), which has field verification powers in accordance with LGEEPA.

The administrative sanctioning regime applicable to non-compliance with conditions is found in articles 171 to 173 of LGEEPA, which establish fines whose amount can reach several thousand days of minimum wage, the revocation of authorizations and the temporary or permanent closure of works. In the context of development projects with third-party financing, the closure or revocation of environmental authorization constitute events of contractual breach that may activate acceleration or early maturity clauses in credit contracts.

From a project management perspective, the operational recommendation is to structure post-resolution compensation obligations as defined deliverables within the project execution plan, with assignment of responsible party, segregated budget and verifiable compliance dates. When the project has institutional financing, it is recommended to explore whether the lender requires the establishment of a fund or reserve for environmental compliance as a condition of disbursement or release of tranches of the credit. This practice, customary in project financing with significant environmental component under international standards, offers the developer certainty regarding the availability of resources necessary to comply with the conditions and reduces the risk of non-compliance due to cash insufficiency in advanced construction stages.

Operational Conclusion

The early integration of environmental compensation analysis in project structuring is not a regulatory formality; it is a first-order financial variable. The optimal scheme requires: forest and ecosystem evaluation of the property before the execution of any binding instrument; projection of compensation scenarios as part of the financial model; and anticipated definition of the compliance strategy, either through deposit to the Forest Fund or through direct actions, considering administrative timelines and the risks of each option. When the MIA resolution imposes conditions that exceed what is technically justified, contentious-administrative litigation and amparo offer avenues of challenge with solid foundation in the principles of proportionality and proper reasoning that govern the administrative act.

IBG Legal has accumulated experience in representing developers before the General Directorate of Forest and Soil Management of SEMARNAT in CUSTF procedures for projects in Quintana Roo, including cases in which the classification of forest surface area or the amount of compensation was subject to technical controversy with the authority. Our team has litigated constitutional remedies before the Collegiate Courts of the XXVII Circuit in matters of environmental impact resolutions and CUSTF, and advises clients on the integration of environmental strategy within the transactional structuring of the project from the due diligence stage through financing closure. This integration of environmental technical capacity and transactional experience in a single team reduces coordination costs and improves the consistency of regulatory strategy before the competent authorities. For specialized advice on this matter, contact us.

Sources and References

Legislation

  • General Law on Ecological Equilibrium and Environmental Protection (LGEEPA), DOF January 28, 1988, last amended DOF January 2022. Articles 28, 30, 35 third paragraph section III (denial authority for EIA), 35 bis 1 (EIA content for works in federal wetlands), 46 to 51 (Protected Natural Areas), 171 to 173 (administrative sanctioning regime).
  • General Law on Sustainable Forest Development (LGDFS), DOF June 5, 2018, last amended DOF April 13, 2020. Article 93 (CUSTF authorization); article 97 (obligation to compensate and deposit to the Mexican Forest Fund).
  • Federal Criminal Code, DOF August 14, 1931, with amendments in force as of 2025. Article 418 (change of forest land use without authorization and forest unlawful acts); article 420 (crimes against wildlife and protected ecosystems).
  • Political Constitution of the United Mexican States, article 4°, fifth paragraph (right to a healthy environment), amendment DOF February 8, 2012.
  • Mexican Official Standard NOM-022-SEMARNAT-2003, DOF April 10, 2003, which establishes the specifications for the preservation, conservation, sustainable use and restoration of coastal wetlands in mangrove areas. Regulatory point 4.3.
  • Environmental Code of the State of Quintana Roo, Official Gazette of the State of Quintana Roo, with amendments in force as of 2023.

Judicial Criteria

  • First Chamber of the Supreme Court of Justice of the Nation: interpretive trend regarding the right to a healthy environment recognized in constitutional article 4°, in the sense that said right operates as a proportional limit to the rights of property and free enterprise, and that environmental compensation measures are constitutionally valid when they maintain proportionality with the accredited impact and are based on technical evidence. This characterization reflects the general line sustained by the First Chamber in matters of third-generation fundamental rights. To invoke specific theses in formal proceedings, scjn.gob.mx).
  • Collegiate Courts of Circuit of the XXVII Circuit (Cancún, Quintana Roo): interpretive trend in matters of constitutional remedy against environmental impact resolutions, in the sense that authorization in environmental impact matters is a discretionary act subject to the principles of precaution and non-regression, and that the burden of proof regarding the sufficiency of compensatory measures falls on the project proponent. For the invocation of specific criteria with registration number,

Official Sources

  • Official Journal of the Federation (DOF): www.dof.gob.mx
  • Official Gazette of the State of Quintana Roo: www.po.qroo.gob.mx
  • SEMARNAT, General Directorate of Forest and Soil Management: tables of value of environmental services for calculating forest compensation by CUSTF. Current values are published by agreement in the DOF and must be verified at the time of preparing the financial model.
  • CONAFOR, Mexican Forest Fund: guidelines for deposits for environmental compensation resulting from CUSTF and environmental services valuation tables by ecosystem type and region. Portal: www.conafor.gob.mx
  • CONANP, National Commission of Natural Protected Areas: management programs of federal Protected Natural Areas in Quintana Roo, including Sian Ka’an Biosphere Reserve, Cozumel Reefs National Park and Tulum National Park. Portal: www.conanp.gob.mx
  • INECC, National Institute of Ecology and Climate Change: technical publications on methodology for valuing forest ecosystem services, including analysis of medium jungle ecosystems in the southeastern region of Mexico. Portal: www.gob.mx/inecc
  • Brañes Ballesteros, Raúl. Manual of Mexican Environmental Law. 2nd ed. Mexican Foundation for Environmental Education / Economic Culture Fund, 2000. Cited for its foundational value in the interpretation of the institutional framework of the LGEEPA; does not address the CUSTF regime under the LGDFS of 2018.
  • Carmona Lara, María del Carmen. General Law on Ecological Balance and Environmental Protection: Comments. Institute of Legal Research, UNAM, 2003. Cited for the interpretation of LGEEPA provisions on environmental impact assessment and the principle of non-regression; does not address the current forestry regime.
  • CONAFOR. Methodology for the Determination of the Value of Environmental Services within the Framework of the Environmental Services Payment Program. National Forestry Commission, current technical publications. Directly relevant to the quantification of compensatory obligations under article 97 of the LGDFS; available on the CONAFOR portal and updated periodically in accordance with agreements published in the DOF.
  • INECC. Studies and technical documents on economic valuation of tropical forest ecosystems in Mexico, with particular reference to the Yucatan Peninsula region, published in the period 2018 to present. Relevant to contextualize the ranges of environmental services value used by SEMARNAT in determining compensation amounts for CUSTF in Quintana Roo.
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