Environmental
By David Jones, MAI, CCIM · Published 2026 · 8 min read
Environmental factors can kill an otherwise feasible project, or force substantial modifications that change the economics entirely. A commercial site with previous industrial use may require remediation costing $200,000 to $2 million+ before construction can begin. A property in a FEMA Special Flood Hazard Area adds flood insurance costs that reduce NOI every year for the life of the loan. A site adjacent to designated wetlands may face permitting delays of 12 to 18 months and mitigation requirements that add 20% to project cost. None of these factors appear in a standard business plan, but all of them affect DSCR and must be integrated into a feasibility analysis.
This guide explains how environmental factors flow into the feasibility study, the distinction between feasibility screening and formal environmental assessment, and how identified environmental issues affect financial projections.
The feasibility study does not replace formal environmental due diligence. Specific environmental assessment products (Phase I ESA, Phase II investigation, wetland delineation, flood certification) are prepared by licensed environmental professionals under defined standards. The feasibility study performs screening-level analysis that identifies environmental factors requiring specialized follow-up, and integrates identified environmental costs and risks into the financial model.
Environmental scope is asset-specific. car wash feasibility studies typically require review of wastewater discharge and prior fuel uses, hotel feasibility studies address older-building issues such as asbestos on conversions, and multifamily feasibility studies on redevelopment sites often need a Phase I before a lender will close.
| Work Product | Who Prepares It | Feasibility Study Role |
|---|---|---|
| Phase I Environmental Site Assessment | Licensed environmental professional per ASTM E1527-21 | Screening-level review of whether Phase I is recommended based on site history; feasibility study does not replace Phase I |
| Phase II investigation and remediation | Licensed environmental professional with lab analysis | Remediation cost estimates (if any) integrated into total project cost |
| Wetland delineation | Licensed wetland scientist per USACE protocols | NWI review identifies whether formal delineation is warranted; does not replace it |
| FEMA flood zone determination | Formal Elevation Certificate by licensed surveyor (for some uses) | NFHL review for flood zone classification; flood insurance cost estimate |
| Stormwater management plan | Licensed civil engineer | Screening for stormwater management needs; cost estimate if required |
| Soil and geotechnical analysis | Licensed geotechnical engineer | Identification of potential soil conditions requiring investigation |
The division of labor matters: the feasibility analyst identifies potential issues, estimates their financial impact using reasonable assumptions, and flags the items requiring professional environmental assessment. The borrower then engages the appropriate specialists based on the flags identified. This two-stage process allows the feasibility analysis to proceed without waiting for potentially weeks-long environmental specialist engagements, while ensuring that environmental factors do not get overlooked.
The first environmental question in any feasibility study is: what was this site used for before? Historical uses determine the probability of environmental contamination, which in turn determines remediation risk, insurance cost, and project timeline.
| Prior Use | Contamination Risk | Typical Assessment Requirement |
|---|---|---|
| Gas station / service station (historical) | High — underground storage tanks, petroleum contamination | Phase I required; Phase II likely; remediation budget $50K to $500K+ |
| Dry cleaner (historical) | High — chlorinated solvents in soil and groundwater | Phase I required; Phase II likely; remediation can be very expensive ($200K to $2M+) |
| Auto repair / body shop | Moderate to high — petroleum, solvents, heavy metals | Phase I required; Phase II dependent on findings |
| Agricultural use (recent) | Low to moderate — pesticides, fuel storage, septic | Phase I recommended; findings determine further scope |
| Industrial manufacturing | High — depends on specific industry | Phase I required; Phase II based on historical operations |
| Residential single-family | Low — typical risks are underground oil tanks | Phase I may not be required; lender-dependent |
| Retail / office (long-term) | Low | Phase I often waived for low-risk sites at lender discretion |
| Undeveloped / virgin land | Very low | Phase I often waived; may require limited environmental review |
| Brownfield site (formally designated) | Confirmed contamination history | Full Phase I and Phase II required; may qualify for cleanup assistance programs |
The feasibility study screens the prior-use profile by reviewing publicly available sources: EPA databases (CERCLIS, RCRA, Brownfields), state environmental agency records, historical aerial photography, Sanborn maps for older sites, and direct inquiry with the property owner. If the screening reveals indicators of potential contamination, the study flags Phase I ESA as a required next step and notes that the project's feasibility conclusion is conditional on Phase I findings.
A brownfield is a site with known or suspected contamination from prior use. Brownfield redevelopment can qualify for specific financing programs (EPA Brownfields grants, state cleanup funds, federal tax incentives) but also introduces remediation costs and timeline risks that greenfield projects do not face.
For SBA loans on brownfield sites, the feasibility study must address several questions. What is the estimated remediation cost (typically from an environmental consultant's Remedial Action Plan)? What is the remediation timeline, and how does it affect the project schedule? Does the remediation qualify for any cleanup assistance programs that offset the cost? What ongoing monitoring or institutional controls will be required after remediation?
The feasibility study integrates the remediation cost into the total project budget, the remediation timeline into the project schedule, and any ongoing monitoring costs into the operating pro forma. A $2.5 million project with $300,000 of remediation becomes a $2.8 million project, which affects loan size, equity injection, and DSCR calculation. A project schedule that requires 6 months of remediation before construction can begin extends the interest reserve requirement and the pre-revenue period.
Federal law (Clean Water Act Section 404) regulates development in wetlands and waters of the United States. Projects on or adjacent to wetlands face permitting requirements from the U.S. Army Corps of Engineers that can add 6 to 18 months to the project schedule and may require mitigation at ratios of 1.5:1 to 3:1 (creating 1.5 to 3 acres of replacement wetlands for each acre filled).
| Wetland Situation | Permit Requirement | Typical Timeline / Cost Impact |
|---|---|---|
| No wetlands on or adjacent to site | None | No timeline or cost impact |
| Wetlands nearby but not on site | Buffer zone requirements; no fill permit needed | Minor site design constraints; minimal cost |
| Small, isolated wetland on site (under 0.5 acres) | Nationwide Permit from USACE | 2 to 4 month permitting process; mitigation may apply |
| Larger wetland or multiple wetlands on site | Individual Permit from USACE | 6 to 18 month permitting process; mitigation required; cost $20K to $200K+ |
| Wetlands in high-value ecological area | Individual Permit with potential denial risk | Permit may be denied; project may need redesign or relocation |
The feasibility study screens for wetland presence using the National Wetlands Inventory (NWI) maps, state wetland databases (which are sometimes more current than the federal NWI), and visual inspection during the site visit. If wetlands are identified, the study flags the need for formal delineation by a licensed wetland scientist and notes the potential permitting timeline. The feasibility conclusion addresses how wetland constraints affect the project's buildable area, construction schedule, and total cost.
Flood zone status is a universal feasibility screening item because flood insurance is mandatory in Special Flood Hazard Areas (SFHAs) and adds a permanent operating expense that affects DSCR.
| FEMA Flood Zone | Risk Level | Insurance Requirement | Typical Annual Cost |
|---|---|---|---|
| Zone X (unshaded) | Minimal risk | Not required by federal law | $0 to $2,000 (optional coverage) |
| Zone X (shaded) / Zone B | Moderate risk | Not federally required; lender may require | $500 to $3,000 |
| Zone A / AE (standard SFHA) | High risk (1% annual flood chance) | Mandatory under National Flood Insurance Program | $2,000 to $15,000+ |
| Zone V / VE (coastal high hazard) | High risk with wave action | Mandatory; elevated construction required | $5,000 to $30,000+ |
| Zone AR / A99 (areas with flood protection) | High risk (behind levee) | Often mandatory; subject to levee certification | $1,500 to $10,000 |
| Zone AH / AO (shallow flooding) | High risk (1 to 3 feet sheet flow) | Mandatory; specific construction requirements | $1,500 to $8,000 |
The financial impact of flood zone classification is direct. A commercial property in Zone AE with $3 million in structure and contents coverage may pay $6,000 to $12,000 annually in flood insurance. Over a 25-year loan term, that is $150,000 to $300,000 of cumulative cost. The feasibility study must include this expense in the operating pro forma for sites in SFHAs, not treat it as a minor adjustment.
Beyond insurance cost, SFHA sites face construction constraints. Structures must be elevated above the Base Flood Elevation (BFE), mechanical equipment must be elevated, and some uses (like below-ground storage) may not be permitted. These constraints add construction cost (typically $50,000 to $300,000 for elevation) and may reduce buildable floor area.
When environmental issues are identified, the feasibility study integrates their cost into the financial model in three places: the total project cost (remediation as a capital item), the project schedule (remediation timeline affecting interest reserve and pre-revenue period), and the operating pro forma (ongoing environmental costs if any).
| Environmental Cost Category | Where It Appears in Pro Forma | Typical Magnitude |
|---|---|---|
| Phase I ESA | Soft cost in total project budget | $2,500 to $8,000 (one-time) |
| Phase II investigation | Soft cost if Phase I recommends it | $10,000 to $75,000 (one-time) |
| Remediation (petroleum contamination) | Hard cost in total project budget | $50,000 to $500,000 |
| Remediation (chlorinated solvents) | Hard cost in total project budget | $200,000 to $2,000,000+ |
| Wetland mitigation | Hard cost; purchased mitigation credits or on-site creation | $15,000 to $300,000+ |
| Flood zone elevation construction premium | Hard construction cost | $50,000 to $300,000 |
| Ongoing flood insurance | Operating expense (annual) | $2,000 to $30,000 per year |
| Ongoing environmental monitoring (post-remediation) | Operating expense (annual, 5-30 years) | $5,000 to $25,000 per year |
| Institutional controls / deed restrictions compliance | Administrative expense | Minimal ongoing cost; affects future sale |
A project with $250,000 of remediation cost and $8,000 of annual flood insurance looks different on paper than the same project without environmental complications. The total project cost increases by $250,000 (affecting loan size and equity injection), the construction timeline extends by the remediation period, and the operating NOI is reduced by $8,000 annually. All three effects flow into the DSCR calculation and must be captured accurately.
SBA lenders and processing centers expect the feasibility study to address environmental factors as part of the site and regulatory assessment section. A feasibility study for a project on a site with known environmental issues that does not address those issues is incomplete. Processing center review will catch the omission, and the loan will be returned for additional analysis.
At minimum, the feasibility study should include the FEMA flood zone determination with a citation to the specific NFHL panel and date reviewed, the NWI wetland review with any findings noted, a prior-use analysis identifying whether environmental contamination concerns exist, a statement of whether Phase I ESA is recommended, and integration of any known environmental costs into the financial model.
The feasibility study does not need to perform formal environmental assessment. It does need to document that environmental factors have been considered and integrated into the financial analysis. A feasibility study silent on environmental factors is a red flag for lenders reviewing the work.
For the full site assessment methodology, see our site and regulatory assessment page. For information on what a feasibility report should contain section by section, see our report structure guide.
Our feasibility studies include environmental screening as a standard component, with flood zone verification, NWI wetland review, and prior-use analysis. Environmental costs are integrated into the financial model to produce a defensible DSCR. Request a scope of work and fixed-fee quote within 24 hours.
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