Private Well WaterA field guide to the water under your house
Limestone & dolomiteFL

Biscayne

A 4,000-square-mile sponge of limestone underneath South Florida — the most productive aquifer in the country and the one most directly threatened by sea-level rise

Where it isRegional view · neighbours dimmed
Coastal lowlands aquifer system — Semiconsolidated sandFloridan aquifer system — Limestone & dolomitePuerto Rico North Coast Limestone aquifer system — Limestone & dolomiteSurficial aquifer system — Sand & gravelBiscayne aquifer — Limestone & dolomite
USGS-mapped footprint: 9,300 km² (3,600 sq mi).
Rock type
Carbonate rock
Mapped area
3,600 sq mi
States
FL
Geology
Highly transmissive Pleistocene karst limestone (Miami Limestone, Fort Thompson Formation)
Status
Saltwater intrusion advancing inland; sea-level-rise-driven retreat of freshwater lens; injection-well disposal contamination concerns
How the water sits in limestone & dolomite

Limestone and dolomite that water slowly dissolves, opening cracks into channels and caves.

What that means for a well: Water can travel through channels fast, with little filtering, so surface pollution arrives quickly. Almost always hard.

water · magnified schematic

What to test for here

Concerns documented for this aquifer, with where each one comes from and whether you'd ever notice it.

The Biscayne aquifer is the shallow karstified limestone aquifer underneath Miami-Dade County, Broward County, and the southern half of Palm Beach County, Florida. It is the principal water supply for about 4 million South Floridians and is widely regarded as one of the most productive aquifers in the world by transmissivity per unit thickness — wells routinely produce thousands of gallons per minute from depths of just 50-100 feet. The aquifer's productivity is the foundation of South Florida's modern existence; without it, Miami would not have grown to be Miami.

The Biscayne is also the US aquifer most directly threatened by sea-level rise. The aquifer is hydraulically connected to the ocean along the Atlantic shoreline; the freshwater "lens" that floats above the deeper saltwater is held in place by the freshwater hydraulic head. As sea level rises and as inland pumping continues, that lens thins and retreats. Saltwater intrusion has been advancing inland for over 80 years, and the rate is accelerating. The City of Hallandale Beach lost three of its eight production wells to saltwater between 2014 and 2019; other coastal Miami-Dade and Broward municipalities face similar trajectories.

What it is, geologically

The Biscayne is built from late Pleistocene limestone — primarily the Miami Limestone (oolitic, very young, ~125,000 years old) and the underlying Fort Thompson Formation (mostly fossiliferous limestone with some interbedded sand). Both units are highly porous and karstified. The aquifer is essentially unconfined — there is no significant overlying confining layer — which makes it vulnerable to surface contamination on a scale matched only by the most extreme karst aquifers like the Edwards.

The aquifer is hydraulically connected to the Everglades to the west; the historical freshwater flow from the Everglades through the aquifer to Biscayne Bay was a key part of the regional hydrology before drainage and development reshaped it. The Comprehensive Everglades Restoration Plan (CERP) is partly aimed at restoring some of those historical freshwater flows, which would also help maintain the aquifer's freshwater head.

Saltwater intrusion: the inland march

The freshwater-saltwater interface in the Biscayne aquifer has been monitored continuously since the 1940s. The interface position is mapped annually by the USGS and the South Florida Water Management District. The pattern over the past half-century:

  • Hallandale Beach — saltwater has advanced inland by over 4 miles since 1950, retiring multiple production wells.
  • Hollywood and surrounding southern Broward County — similar pattern.
  • Northern Miami-Dade — multiple coastal cities have moved their wellfields inland multiple times.
  • Florida Keys — Biscayne aquifer wells in the upper Keys have largely been abandoned; the Keys are supplied by surface water piped from the mainland.

For private well owners — relatively rare in Miami-Dade and Broward, but more common in agricultural southern Miami-Dade (the Homestead/Florida City area) — chloride trend monitoring is essential. See saltwater intrusion.

Injection-well contamination concerns

South Florida disposes of treated wastewater through deep-injection wells that inject the effluent into the brackish "boulder zone" below the freshwater aquifer. The injection wells were designed on the assumption that the boulder zone was hydraulically isolated from the overlying Biscayne. Multiple lines of evidence accumulated through the 1990s-2000s showed that this assumption is incorrect in some areas — treated wastewater has been documented migrating upward into the Biscayne aquifer, particularly through fault zones and karst conduits. The implications for drinking water quality are debated and the regulatory response has been gradual.

Water quality

  • Saltwater intrusion markers (chloride, sodium, sulfate) — the dominant concern. See saltwater intrusion.
  • Bacteria — karst conduits and the lack of a confining layer mean surface contamination reaches wells quickly. See bacteria.
  • Nitrates — agricultural and septic-source; relevant in southern Miami-Dade ag areas.
  • Hardness — high (limestone-derived). Most homes have softeners.
  • Iron, hydrogen sulfide — present in deeper portions of the aquifer.
  • Pharmaceuticals and personal-care products (PPCPs) — emerging concern from the injection-well migration story; not regulated; detection at trace concentrations.
If you're on a private well in southern Miami-Dade or Broward County and within roughly 5 miles of the coast, the chloride trend in your water over the next 10 years matters more than the absolute value today. Test annually; keep records. South Florida coastal real estate is increasingly being valued partly on water-quality trajectory; documented chloride trend data has economic relevance for property sales.

PFAS risk modeling

The USGS 2024 national PFAS-in-groundwater predictive model estimates a 41.4% mean probability of detecting any PFAS compound at typical private-well drinking-water depth across the Biscayne. Roughly 30.3% of the aquifer's area falls in the model's >50% probability band — land where a freshly drilled domestic well is predicted more likely than not to show some detectable PFAS. That is above the national CONUS aquifer median of 19%, and places the Biscayne in the top 10% of CONUS Principal Aquifers for predicted PFAS detection.

This is a 1 km-resolution statistical prediction, not a measurement of any specific well. What PFAS is and how it gets into groundwater → · How to test a private well for PFAS → · Full state-and-aquifer breakdown with methodology →

Predicted chance a new private well detects PFAS — 58 aquifers
0%25%50%75%100%median 19%Upper carbonate aquifer: 7%Snake River Plain basaltic-rock aquifers: 9%Pacific Northwest basaltic-rock aquifers: 9%Columbia Plateau basaltic-rock aquifers: 10%Basin and Range carbonate-rock aquifers: 10%Paleozoic aquifers: 10%Colorado Plateaus aquifers: 11%Roswell Basin aquifer system: 12%Texas coastal uplands aquifer system: 12%Arbuckle-Simpson aquifer: 12%Edwards-Trinity aquifer system: 13%Lower Cretaceous aquifers: 13%Pacific Northwest basin-fill aquifers: 13%Ada-Vamoosa aquifer: 13%Upper Tertiary aquifers: 13%Mississippi embayment aquifer system: 14%Basin and Range basin-fill aquifers: 14%Lower Tertiary aquifers: 15%Northern Rocky Mountains Intermontane Basins aquifer system: 15%High Plains aquifer: 15%Southern Nevada volcanic-rock aquifers: 16%Rush Springs aquifer: 16%Rio Grande aquifer system: 16%Ozark Plateaus aquifer system: 16%Columbia Plateau basin-fill aquifers: 17%Pecos River Basin alluvial aquifer: 18%Snake River Plain basin-fill aquifers: 18%Upper Cretaceous aquifers: 19%Cambrian-Ordovician aquifer system: 19%Mississippi River Valley alluvial aquifer: 19%Seymour aquifer: 19%Denver Basin aquifer system: 19%Central Valley aquifer system: 19%Southeastern Coastal Plain aquifer system: 20%Coastal lowlands aquifer system: 21%Blaine aquifer: 21%Surficial aquifer system: 22%Jacobsville aquifer: 23%Mississippian aquifers: 23%Silurian-Devonian aquifers: 24%Pennsylvanian aquifers: 27%Floridan aquifer system: 28%Valley and Ridge aquifers: 28%Piedmont and Blue Ridge crystalline-rock aquifers: 30%Central Oklahoma aquifer: 30%Marshall aquifer: 30%Castle Hayne aquifer: 30%Northern Atlantic Coastal Plain aquifer system: 31%New York and New England carbonate-rock aquifers: 33%New York sandstone aquifers: 36%California Coastal Basin aquifers: 37%Valley and Ridge carbonate-rock aquifers: 37%Willamette Lowland basin-fill aquifers: 37%Ordovician aquifers: 40%Piedmont and Blue Ridge carbonate-rock aquifers: 41%Puget Sound aquifer system: 42%Early Mesozoic basin aquifers: 44%Biscayne aquifer: 41%41%

Black dot: this aquifer. Grey: every other mapped aquifer in the lower 48. Model estimate, not measurements of wells.

Sources

  • USGS Professional Paper 1403-C — Hydrogeology of the Biscayne Aquifer
  • USGS Scientific Investigations Report 2014-5025 — Saltwater Intrusion in the Biscayne Aquifer
  • Miami-Dade Water and Sewer Department — Annual Water Quality Reports
  • South Florida Water Management District — Saltwater Interface Monitoring Network
  • US EPA — Underground Injection Control Program: South Florida Class I Wells
  • Bloetscher et al. — Sea Level Rise and Coastal Aquifers (J Water Resour Plan Manag, 2010)