Infiltration Feasibility¶
Infiltration feasibility is the combined assessment that determines whether a site can support stormwater infiltration into native soils. It integrates soil permeability, SHWT depth, groundwater mounding risk, site contamination history, and geologic conditions into a single go/no-go decision that governs BMP selection and groundwater recharge compliance.
Source: NJ Stormwater BMP Manual, Chapters 6, 9, 12, 13; N.J.A.C. 7:8-5.3, 7:8-5.4
Concept Explanation¶
No single soil or site parameter determines whether infiltration is feasible. Instead, the engineer must evaluate multiple constraints simultaneously and arrive at one of three outcomes:
- Full infiltration feasible — the site can support infiltration-based GI BMPs without underdrains, qualifying for groundwater recharge credit and GI volumetric reduction compliance
- Partial infiltration feasible — some infiltration is possible but constraints require design modifications (e.g., underdrain with elevated outlet creating an internal water storage zone)
- Infiltration infeasible — site conditions prohibit infiltration entirely; the designer must document the infeasibility finding and propose Non-GI alternatives
The 2026 amendments to N.J.A.C. 7:8 formalized the requirement that engineers must document GI feasibility analysis before proposing Non-GI alternatives. Generic statements ("GI is infeasible due to site constraints") are no longer acceptable. The analysis must include specific soil investigation data, SHWT determination, and identification of the constraint(s) that preclude infiltration.
Combined Assessment Framework¶
The following decision framework represents the standard evaluation sequence for infiltration feasibility:
Step 1: Soil Permeability
K_sat >= 0.5 in/hr AND HSG A or B? --> Proceed to Step 2
K_sat < 0.5 in/hr OR HSG C/D? --> Infiltration limited; underdrain required
HSG D with K_sat < 0.05 in/hr? --> Infiltration generally infeasible
Step 2: Seasonal High Water Table
SHWT >= 2 ft below BMP bottom? --> Proceed to Step 3
SHWT < 2 ft below BMP bottom? --> Infiltration infeasible at proposed depth
Options: raise BMP, reduce depth, underdrain
Step 3: Groundwater Mounding
Post-mounding WT still >= 2 ft --> Proceed to Step 4
below BMP bottom?
Mound reduces separation < 2 ft? --> Reduce infiltration volume, add underdrain,
or split into smaller distributed practices
Step 4: Site Prohibitions
Contaminated soils? --> Infiltration prohibited (NJDEP review)
Karst geology? --> Infiltration prohibited or severely restricted
Stormwater hotspot? --> Infiltration prohibited
None of the above? --> INFILTRATION FEASIBLE
Infiltration vs. Underdrain Decision¶
When full infiltration is not feasible, the designer must choose between:
| Design Option | When to Use | Recharge Credit | GI Credit |
|---|---|---|---|
| Full infiltration (no underdrain) | K_sat adequate, SHWT adequate, no prohibitions | Yes — full recharge credit | Yes — volumetric reduction per Ch. 14 |
| Underdrain with elevated outlet (IWZ) | Moderate soils; partial infiltration desired | Partial — credit for infiltrated fraction only | Partial — volumetric reduction for retained volume |
| Underdrain at invert (no retention) | Poor soils (HSG C/D), shallow SHWT, or prohibitions | None — no recharge credit | Water quality treatment only; does not satisfy GI volumetric standard |
| Lined system with underdrain | Contaminated soils, hotspots, or karst | None — liner prevents infiltration | Water quality treatment only |
The 2026 BMP Manual explicitly states that BMPs providing recharge credit must not use impermeable liners. The liner prohibition is absolute for practices counting toward recharge compliance.
Engineering Evaluation¶
Required Investigations¶
The 2026 Soil Investigation Protocol (Chapter 12) requires the following site data to support the infiltration feasibility determination:
| Investigation | Purpose | Minimum Standard (2026) |
|---|---|---|
| Soil borings / test pits | HSG classification, soil profile, SHWT | 1 per BMP footprint (up to 5,000 sq ft); +1 per additional 5,000 sq ft; 72 in below BMP bottom |
| In-situ permeability testing | Design K_sat | Falling-head permeameter or ASTM D5126; geometric mean with 50% safety factor |
| SHWT determination | Separation verification | Redoximorphic feature identification by qualified professional |
| Mounding analysis | Groundwater rise evaluation | Hantush method or equivalent when triggers are met (high K_sat, shallow WT, large volumes) |
| Environmental site assessment | Contamination screening | Phase I ESA minimum for commercial/industrial sites; Phase II if contamination suspected |
| Geologic mapping review | Karst / bedrock identification | NJGS geologic maps; borings to confirm depth to bedrock |
Documenting the Feasibility Finding¶
Under the 2026 rules, the Stormwater Management Report must include a GI Feasibility Analysis section containing:
- Site plan showing proposed BMP locations and soil investigation points
- Boring logs with soil descriptions, Munsell color notation, and redox feature depths
- K_sat test results with safety factor calculation
- SHWT depth determination and available separation calculation
- Mounding analysis results (if triggered)
- Hotspot screening determination
- Contamination screening results
- Conclusion: feasible, partially feasible, or infeasible — with specific constraint(s) identified
Prohibitions: When Infiltration Is Not Permitted¶
Certain site conditions create absolute prohibitions on stormwater infiltration:
Karst Geology
Sites underlain by carbonate bedrock (limestone, dolomite) are susceptible to sinkhole formation when concentrated infiltration dissolves subsurface rock. The NJ BMP Manual prohibits or severely restricts infiltration in mapped karst areas. Where karst is identified, the designer must use lined or underdrained systems that prevent percolation to bedrock.
Contaminated Soils
Infiltrating stormwater through contaminated soils can mobilize pollutants and carry them to groundwater. Sites with known or suspected contamination (brownfields, former industrial uses, underground storage tank sites) require NJDEP review before any infiltration practice is approved. In most cases, infiltration is prohibited until remediation is complete.
Stormwater Hotspots
Locations where runoff carries pollutants at concentrations that could contaminate groundwater — fueling stations, vehicle maintenance yards, hazardous material storage areas, high-traffic industrial facilities. Full hotspot classification prohibits infiltration entirely. Lower-risk transitional areas may allow infiltration with pretreatment, but this requires case-by-case NJDEP determination.
High Water Table (< 2 ft separation)
While not an absolute prohibition in all cases (the BMP can sometimes be raised or redesigned), a SHWT that cannot be separated from the BMP bottom by 2 feet effectively prohibits infiltration at that location.
Affected BMPs¶
The infiltration feasibility assessment applies to every practice that relies on percolation into native soils:
| BMP | Feasibility Outcome | Design Path | Link |
|---|---|---|---|
| Bioretention (no underdrain) | Requires full feasibility | Full infiltration + recharge credit | Bioretention |
| Bioretention (with underdrain) | Used when partial or no infiltration | Water quality treatment; partial or no recharge | Bioretention |
| Infiltration basins | Requires full feasibility; most demanding | Full infiltration in HSG A/B soils only | BMP Library |
| Dry wells | Requires full feasibility | Point-source infiltration for rooftop runoff | BMP Library |
| Pervious pavement | Requires feasibility for unlined subbase | Underdrain alternative for poor soils | BMP Library |
| Extended detention basins | Not dependent on infiltration | Non-GI; detention and treatment focus | BMP Library |
Related Regulations¶
N.J.A.C. 7:8 Rule Citations¶
| Rule Section | Topic | Relevance to Infiltration Feasibility |
|---|---|---|
| N.J.A.C. 7:8-5.3 | Green Infrastructure Requirement | Documented feasibility analysis required before proposing Non-GI; hierarchical GI application |
| N.J.A.C. 7:8-5.4(a) | Groundwater Recharge | Recharge compliance depends on infiltration feasibility; technical infeasibility finding available when conditions preclude infiltration |
| N.J.A.C. 7:8-5.2 | Soil Testing (2026) | Defines investigation requirements that feed the feasibility determination |
BMP Manual Chapter Citations¶
- Chapter 12 — Soil Testing Criteria: Soil investigation protocol, K_sat testing methodology, SHWT determination, boring requirements
- Chapter 13 — Groundwater Mounding Analysis: Mounding assessment methods and acceptance criteria
- Chapter 6 — Groundwater Recharge: Recharge standard, HSG-based recharge rates, separation requirements, hotspot prohibition, liner prohibition
- Chapter 9 — Small-Scale GI BMPs: Siting constraints for bioretention and other small-scale practices that depend on infiltration feasibility
- Chapter 14 — Volumetric Reduction Standards (2026): Volumetric reduction credit is available only when infiltration feasibility is confirmed