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Everglades

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The Everglades is a natural region of flooded grasslands in the southern portion of the U.S. state of Florida, comprising the southern half of a large drainage basin within the Neotropical realm. The system begins near Orlando with the Kissimmee River, which discharges into the vast but shallow Lake Okeechobee. Water leaving the lake in the wet season forms a slow-moving river 60 miles (97 km) wide and over 100 miles (160 km) long, flowing southward across a limestone shelf to Florida Bay at the southern end of the state. The Everglades experiences a wide range of weather patterns, from frequent flooding in the wet season to drought in the dry season. Throughout the 20th century, the Everglades suffered significant loss of habitat and environmental degradation.

Key Information

Human habitation in the southern portion of the Florida peninsula dates to 15,000 years ago. Before European colonization, the region was dominated by the native Calusa and Tequesta tribes. With Spanish colonization, both tribes declined gradually during the following two centuries. The Seminole, formed from mostly Creek people who had been warring to the North, assimilated other peoples and created a new culture after being forced from northern Florida into the Everglades during the Seminole Wars of the early 19th century. After adapting to the region, they were able to resist removal by the United States Army.

Migrants to the region who wanted to develop plantations first proposed draining the Everglades in 1848, but no work of this type was attempted until 1882. Canals were constructed throughout the first half of the 20th century, and spurred the South Florida economy, prompting land development. In 1947, Congress formed the Central and Southern Florida Flood Control Project, which built 1,400 miles (2,300 km) of canals, levees, and water control devices. The Miami metropolitan area grew substantially at this time and Everglades water was diverted to cities. Portions of the Everglades were transformed into farmland, where the primary crop was sugarcane. Approximately 50 percent of the original Everglades has been developed as agricultural or urban areas.[2]

Following this period of rapid development and environmental degradation, the ecosystem began to receive notable attention from conservation groups in the 1970s. Internationally, UNESCO and the Ramsar Convention designated the Everglades a Wetland Area of Global Importance. The construction of a large airport 6 miles (10 km) north of Everglades National Park was blocked when an environmental study found that it would severely damage the South Florida ecosystem. With heightened awareness and appreciation of the region, restoration began in the 1980s with the removal of a canal that had straightened the Kissimmee River. However, development and sustainability concerns have remained pertinent in the region. The deterioration of the Everglades, including poor water quality in Lake Okeechobee, was linked to the diminishing quality of life in South Florida's urban areas. In 2000 the Comprehensive Everglades Restoration Plan was approved by Congress to combat these problems, which at that time was considered the most expensive and comprehensive environmental restoration attempt in history; however, implementation faced political complications.

Names

[edit]
This map made by the U.S. military shows the term "Everglades" was in use by 1857.

The first written record of the Everglades was on Spanish maps made by cartographers who had not seen the land. They named the unknown area between the Gulf and Atlantic coasts of Florida Laguna del Espíritu Santo ("Lake of the Holy Spirit").[3] The area was featured on maps for decades without having been explored. Writer James Grant Forbes stated in 1811, "The Indians represent [the Southern points] as impenetrable; and the [British] surveyors, wreckers, and coasters, had not the means of exploring beyond the borders of the sea coast, and the mouths of rivers".[4]

British surveyor John Gerard de Brahm, who mapped the coast of Florida in 1773, called the area "River Glades". The name "Everglades" first appeared on a map in 1823, although it was also spelled as "Ever Glades" as late as 1851.[5] The Seminole call it Pahokee, meaning "Grassy Water".[6] The region was labeled "Pa-hai-okee" on a U.S. military map from 1839, although it had earlier been called "Ever Glades" throughout the Second Seminole War.[4]

A 2007 survey by geographers Ary J. Lamme and Raymond K. Oldakowski found that the "Glades" has emerged as a distinct vernacular region of Florida. It comprises the interior areas and southernmost Gulf Coast of South Florida, largely corresponding to the Everglades itself. It is one of the most sparsely populated areas of the state.[7]

Geology

[edit]

The geology of South Florida, together with a warm, wet, subtropical/tropical climate, provides conditions well-suited for a large marshland ecosystem. Layers of porous and permeable limestone create water-bearing rock and soil that affect the climate, weather, and hydrology of South Florida.[8] The properties of the rock underneath the Everglades can be explained by the geologic history of the state. The crust underneath Florida was at one point part of the African region of the supercontinent Gondwana. About 300 million years ago, North America merged with Africa, connecting Florida with North America. Volcanic activity centered on the eastern side of Florida covered the prevalent sedimentary rock with igneous rock. Continental rifting began to separate North America from Gondwana about 180 million years ago.[9] When Florida was part of Africa, it was initially above water, but during the cooler Jurassic Period, the Florida Platform became a shallow marine environment in which sedimentary rocks were deposited. Through the Cretaceous Period, most of Florida remained a tropical sea floor of varying depths.[10] The peninsula has been covered by seawater at least seven times since the bedrock formed.[11]

Limestone and aquifers

[edit]

Fluctuating sea levels compressed numerous layers of calcium carbonate, sand, and shells. The resulting permeable limestone formations that developed between 25 million and 70 million years ago created the Floridan aquifer, which serves as the main source of fresh water for the northern portion of Florida. However, this aquifer lies beneath thousands of feet of impermeable sedimentary rock from Lake Okeechobee to the southern tip of the peninsula.[12]

A satellite image of the Everglades, taken in March 2019
Limestone formations in South Florida. Source: U.S. Geological Survey

Five geologic formations form the surface of the southern portion of Florida: the Tamiami Formation, Caloosahatchee Formation, Anastasia Formation, Miami Limestone, and the Fort Thompson Formation. The Tamiami Formation is a compression of highly permeable light-colored fossiliferous sands and pockets of quartz, 150 feet (46 m) thick. It is named for the Tamiami Trail that follows the upper bedrock of the Big Cypress Swamp, and underlies the southern portion of the Everglades. Between the Tamiami Formation and Lake Okeechobee is the Caloosahatchee Formation, named for the river over it. Much less permeable, this formation is highly calcitic and is composed of sandy shell marl, clay, and sand. Water underneath the Caloosahatchee Formation is typically very mineralized. Both the Tamiami and Caloosahatchee Formations developed during the Pliocene Epoch.[13][14]

Surrounding the southern part of Lake Okeechobee is the Fort Thompson Formation, made of dense, hard limestone, shells, and sand. Rain water is less likely to erode the limestone to form solution holes—smaller versions of sinkholes that do not intersect with the water table. In this formation the beds are generally impermeable.[15] Underneath the metropolitan areas of Palm Beach County is the Anastasia Formation, composed of shelly limestone, coquina, and sand representing a former mangrove or salt marsh. The Anastasia Formation is much more permeable and filled with pocks and solution holes.[15] The Fort Thompson and Anastasia Formations, and Miami Limestone and (x), were formed during the Sangamonian interglacial period.[16]

The geologic formations that have the most influence on the Everglades are the Miami Limestone and the Fort Thompson Formation. The Miami Limestone has two facies. The Miami Oolite facies, which underlies the Atlantic Coastal Ridge from southern Palm Beach County to southern Miami-Dade County, is made up of ooids: tiny formations of egg-shaped concentric shells and calcium carbonate, formed around a single grain of sand or shell fragment. The other facies, which underlies the eastern lower Everglades (in Miami-Dade County and part of Monroe County) consists of fossilized bryozoan organisms.[17] The unique structure was some of the first material used in housing in early 20th-century South Florida. The composition of this sedimentary formation affects the hydrology, plant life, and wildlife above it: the rock is especially porous and stores water during the dry season in the Everglades, and its chemical composition determines the vegetation prevalent in the region. The Miami Oolite facies also acts to impede flow of water from the Everglades to the ocean between Fort Lauderdale and Coot Bay (near Cape Sable).[18]

The metropolitan areas of Miami, Fort Lauderdale, and West Palm Beach are located on a rise in elevation along the eastern coast of Florida, called the Miami Rock Ridge, a relict oolite shoal deposited on top of the Anastasia Formation.[19] Along the western border of the Big Cypress Swamp is the Immokolee Ridge (or Immokolee Rise), a slight rise of compressed sand that divides the runoff between the Caloosahatchee River and The Big Cypress.[20] This slight rise in elevation on both sides of the Everglades creates a basin, and forces water that overflows Lake Okeechobee to creep toward the southwest.[21] Under both the Miami Limestone formation and the Fort Thompson limestone lies the Biscayne Aquifer, a surface aquifer that serves as the Miami metropolitan area's fresh water source. Rainfall and stored water in the Everglades replenish the Biscayne Aquifer directly.[16]

With the rise of sea levels that occurred during the Pleistocene approximately 17,000 years ago, the runoff of water from Lake Okeechobee slowed and created the vast marshland that is now known as the Everglades. Slower runoff also created an accumulation of almost 18 feet (5.5 m) of peat in the area. The presence of such peat deposits, dated to about 5,000 years ago, is evidence that widespread flooding had occurred by then.[22]

Hydrology

[edit]
Predevelopment flow direction of water from Lake Okeechobee to Florida Bay Source: U.S. Geological Survey

The consistent Everglades flooding is fed by the extensive Kissimmee, Caloosahatchee, Miami, Myakka, and Peace Rivers in central Florida. The Kissimmee River is a broad floodplain that empties directly into Lake Okeechobee, which at 730 square miles (1,900 km2) with an average depth of 9 feet (2.7 m), is a vast but shallow lake.[23] Soil deposits in the Everglades basin indicate that peat is deposited where the land is flooded consistently throughout the year. Calcium deposits are left behind when flooding is shorter. The deposits occur in areas where water rises and falls depending on rainfall, as opposed to water being stored in the rock from one year to the next. Calcium deposits are present where more limestone is exposed.[24]

The area from Orlando to the tip of the Florida peninsula was at one point a single drainage unit. When rainfall exceeded the capacity of Lake Okeechobee and the Kissimmee River floodplain, it spilled over and flowed in a southwestern direction to empty into Florida Bay. Prior to urban and agricultural development in Florida, the Everglades began at the southern edge of Lake Okeechobee and flowed for approximately 100 miles (160 km), emptying into the Gulf of Mexico. The limestone shelf is wide and slightly angled instead of having a narrow, deep channel characteristic of most rivers. The vertical gradient from Lake Okeechobee to Florida Bay is about 2 inches (5.1 cm) per mile, creating an almost 60-mile (97 km) wide expanse of river that travels about one-half mile (0.80 km) a day.[25] This slow movement of a broad, shallow river is known as sheetflow, and gives the Everglades its nickname, River of Grass. Water leaving Lake Okeechobee may require months or years to reach its final destination, Florida Bay. The sheetflow travels so slowly that water is typically stored from one wet season to the next in the porous limestone substrate. The ebb and flow of water has shaped the land and every ecosystem in South Florida throughout the Everglades' estimated 5,000 years of existence. The motion of water defines plant communities and how animals adapt to their habitats and food sources.[26]

Climate

[edit]
Hurricane Charley in 2004 moving ashore on South Florida's Gulf of Mexico coast

The climate of South Florida is located across the broad transition zone between subtropical and tropical climates (Koppen Aw, Am and Cfa). Like most regions with this climate type, there are two basic seasons – a "dry season" (winter) which runs from November through April, and a "wet season" (summer) which runs from May through October. About 70% of the annual rainfall in south Florida occurs in the wet season – often as brief but intense tropical downpours. The dry season sees little rainfall and dew points and humidity are often quite low. The dry season can be severe at times, as wildfires and water restrictions are often in place.

The annual range of temperatures in south Florida and the Everglades is rather small‌less than 20 °F or 11°C‌ranging from a monthly mean temperature of around 65 °F (18 °C) in January to 83 °F (28 °C) in July. High temperatures in the hot and wet season (summer) typically exceed 90 °F (32 °C) across inland south Florida (although coastal locations are cooled by winds from the Gulf of Mexico and the Atlantic Ocean), while high temperatures in the dry winter season average from 70 to 79 °F (21 to 26 °C). Frost and freeze are rare across south Florida and the Everglades; annually coastal cities like Miami and Naples report zero days with frost, although a few times each decade low temperatures may fall between 30 and 40 °F (−1 and 4 °C) across South Florida. The plant hardiness zones are 10a north with an average annual extreme minimum air temperature of 30 to 35 °F (−1 to +2 °C), and 10b south with an average annual extreme minimum air temperature of 35 to 40 °F (2 to 4 °C).[27] Annual rainfall averages approximately 62 inches (160 cm), with the Eastern Coastal Ridge receiving the majority of precipitation and the area surrounding Lake Okeechobee receiving about 48 inches (120 cm).[28]

Unlike any other wetland system on earth, the Everglades are sustained primarily by the atmosphere.[29] Evapotranspiration‌the sum of evaporation and plant transpiration from the Earth's land surface to atmosphere‌associated with thunderstorms, is the key mechanism by which water leaves the region. During a year unaffected by drought, the rate may reach 40 inches (100 cm) a year. When droughts take place, the rate may peak at over 50 inches (130 cm), and exceed the amount of rainfall.[30] As water leaves an area through evaporation from groundwater or from plant matter, activated primarily by solar energy, it is then moved by wind patterns to other areas that border or flow into the Everglades watershed system. Evapotranspiration is responsible for approximately 70– 90% of water entering undeveloped wetland regions in the Everglades.[31]

Precipitation during the wet season is primarily caused by air mass thunderstorms and the easterly flow out of the subtropical high (Bermuda High). Intense daytime heating of the ground causes the warm moist tropical air to rise, creating the afternoon thundershowers typical of tropical climates. Across South Florida and the Everglades, 2:00 pm is the mean time of daily thundershower occurrence. Late in the wet season (August and September), precipitation levels reach their highest levels as tropical depressions and lows add to daily rainfall. Occasionally, tropical lows can become severe tropical cyclones and cause significant damage when they make landfall across south Florida. Tropical storms average one a year, and major hurricanes about once every ten years. Between 1871 and 1981, 138 tropical cyclones struck directly over or close to the Everglades.[28] Strong winds from these storms disperse plant seeds and replenish mangrove forests, coral reefs, and other ecosystems. Dramatic fluctuations in precipitation are characteristic of the South Florida climate. Droughts, floods, and tropical cyclones are part of the natural water system in the Everglades.[31]

Climate data for 36 mi WNW Miami, Miami-Dade County, Florida (1981 – 2010 averages).
Month Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec Year
Mean daily maximum °F (°C) 76.7
(24.8)
78.9
(26.1)
81.1
(27.3)
84.9
(29.4)
88.6
(31.4)
90.8
(32.7)
91.9
(33.3)
92.0
(33.3)
90.4
(32.4)
87.1
(30.6)
82.1
(27.8)
78.4
(25.8)
85.3
(29.6)
Daily mean °F (°C) 66.5
(19.2)
68.6
(20.3)
70.8
(21.6)
74.0
(23.3)
78.2
(25.7)
82.0
(27.8)
83.5
(28.6)
83.9
(28.8)
82.8
(28.2)
79.5
(26.4)
73.8
(23.2)
69.0
(20.6)
76.1
(24.5)
Mean daily minimum °F (°C) 56.2
(13.4)
58.3
(14.6)
60.5
(15.8)
63.1
(17.3)
67.7
(19.8)
73.1
(22.8)
75.1
(23.9)
75.8
(24.3)
75.3
(24.1)
71.8
(22.1)
65.4
(18.6)
59.5
(15.3)
66.9
(19.4)
Average precipitation inches (mm) 1.62
(41)
2.03
(52)
2.75
(70)
2.56
(65)
4.45
(113)
8.70
(221)
7.11
(181)
7.42
(188)
7.01
(178)
4.02
(102)
2.08
(53)
1.38
(35)
51.13
(1,299)
Average relative humidity (%) 74.6 73.0 70.7 68.3 70.7 75.3 74.7 76.2 77.6 76.6 75.6 75.4 74.1
Source: PRISM Climate Group[32]
Month Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec Year
Average Dew Point °F 58.2 59.6 60.8 62.9 67.9 73.4 74.6 75.6 75.1 71.5 65.6 60.9 67.2
Average Dew Point °C 14.6 15.3 16.0 17.2 19.9 23.0 23.7 24.2 23.9 21.9 18.7 16.1 19.6
Source = PRISM Climate Group[33]
Climate data for Royal Palm Ranger Station, Florida, 1991–2020 normals, extremes 1949–present
Month Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec Year
Record high °F (°C) 92
(33)
97
(36)
101
(38)
102
(39)
107
(42)
104
(40)
102
(39)
103
(39)
105
(41)
106
(41)
99
(37)
95
(35)
107
(42)
Mean maximum °F (°C) 86.8
(30.4)
88.4
(31.3)
91.2
(32.9)
93.3
(34.1)
95.9
(35.5)
97.1
(36.2)
97.3
(36.3)
97.3
(36.3)
96.8
(36.0)
94.7
(34.8)
90.1
(32.3)
87.5
(30.8)
99.4
(37.4)
Mean daily maximum °F (°C) 78.0
(25.6)
80.9
(27.2)
83.3
(28.5)
86.4
(30.2)
89.4
(31.9)
91.1
(32.8)
92.5
(33.6)
92.6
(33.7)
91.3
(32.9)
88.0
(31.1)
83.2
(28.4)
80.0
(26.7)
86.4
(30.2)
Daily mean °F (°C) 66.6
(19.2)
68.7
(20.4)
70.7
(21.5)
74.2
(23.4)
78.0
(25.6)
81.6
(27.6)
83.0
(28.3)
83.5
(28.6)
82.8
(28.2)
79.4
(26.3)
73.5
(23.1)
69.3
(20.7)
75.9
(24.4)
Mean daily minimum °F (°C) 55.1
(12.8)
56.5
(13.6)
58.0
(14.4)
62.0
(16.7)
66.6
(19.2)
72.0
(22.2)
73.5
(23.1)
74.3
(23.5)
74.2
(23.4)
70.9
(21.6)
63.8
(17.7)
58.6
(14.8)
65.5
(18.6)
Mean minimum °F (°C) 38.9
(3.8)
41.7
(5.4)
43.7
(6.5)
50.3
(10.2)
58.0
(14.4)
67.8
(19.9)
70.3
(21.3)
71.0
(21.7)
70.8
(21.6)
61.3
(16.3)
52.1
(11.2)
44.5
(6.9)
35.8
(2.1)
Record low °F (°C) 24
(−4)
29
(−2)
31
(−1)
37
(3)
49
(9)
50
(10)
66
(19)
66
(19)
64
(18)
49
(9)
31
(−1)
27
(−3)
24
(−4)
Average precipitation inches (mm) 1.70
(43)
1.82
(46)
1.93
(49)
2.85
(72)
5.84
(148)
9.00
(229)
6.82
(173)
8.57
(218)
9.01
(229)
5.55
(141)
2.39
(61)
1.88
(48)
57.36
(1,457)
Average precipitation days (≥ 0.01 in) 6.6 6.5 6.7 6.3 10.9 17.2 17.2 19.2 18.3 12.6 7.8 6.6 135.9
Source: NOAA[34][35]

Formative and sustaining processes

[edit]

The Everglades are a complex system of interdependent ecosystems. Marjory Stoneman Douglas described the area as a "River of Grass" in 1947, though that metaphor represents only a portion of the system. The area recognized as the Everglades, prior to drainage, was a web of marshes and prairies 4,000 square miles (10,000 km2) in size.[36] Borders between ecosystems are subtle or imperceptible. These systems shift, grow and shrink, die, or reappear within years or decades. Geologic factors, climate, and the frequency of fire help to create, maintain, or replace the ecosystems in the Everglades.

Water

[edit]
A storm over the Shark River in the Everglades, 1966

Water is the dominant force in the Everglades, shaping the land, vegetation, and animal life in South Florida. Starting at the last glacial maximum, 21,000 years ago, continental ice sheets retreated and sea levels rose. This submerged portions of the Florida peninsula and caused the water table to rise. Fresh water saturated the limestone that underlies the Everglades, eroding some of it away, and created springs and sinkholes. The abundance of fresh water allowed new vegetation to take root, and formed convective thunderstorms over the land through evaporation.[37][38]

As rain continued to fall, the slightly acidic rainwater dissolved the limestone. As limestone wore away, the groundwater came into contact with the land surface and created a massive wetland ecosystem.[37] Although the region appears flat, weathering of the limestone created slight valleys and plateaus in some areas. These plateaus rise and fall only a few inches, but on the subtle South Florida topography these small variations affect both the flow of water and the types of vegetation that can take hold.[39]

Rock

[edit]
Uneven limestone formations in an Everglades sawgrass prairie

The underlying bedrock or limestone of the Everglades basin affects the hydroperiod, or how long an area within the region stays flooded throughout the year.[37] Longer hydroperiods are possible in areas that were submerged beneath seawater for longer periods of time, while the geology of Florida was forming. More water is held within the porous ooids and limestone than older types of rock that spent more time above sea level.[40] A hydroperiod of ten months or more fosters the growth of sawgrass, whereas a shorter hydroperiod of six months or less promotes beds of periphyton, a growth of algae and other microscopic organisms. There are only two types of soil in the Everglades, peat and marl. Where there are longer hydroperiods, peat builds up over hundreds or thousands of years due to many generations of decaying plant matter.[41] Where periphyton grows, the soil develops into marl, which is more calcitic in composition.

Initial attempts at developing agriculture near Lake Okeechobee were successful, but the nutrients in the peat were rapidly removed. In a process called soil subsidence, oxidation of peat causes loss of volume.[42] Bacteria decompose dead sawgrass slowly underwater without oxygen. When the water was drained in the 1920s and bacteria interacted with oxygen, an aerobic reaction occurred. Microorganisms degraded the peat into carbon dioxide and water. Some of the peat was burned by settlers to clear the land. Some homes built in the areas of early farms had to have their foundations moved to stilts as the peat deteriorated; other areas lost approximately 8 feet (2.4 m) of soil depth.[43]

Fire

[edit]
Wildfire photographed in 1922

Fire is an important element in the natural maintenance of the Everglades. The majority of fires are caused by lightning strikes from thunderstorms during the wet season. Their effects are largely superficial, and serve to foster specific plant growth: sawgrass will burn above water, but the roots are preserved underneath. Fire in the sawgrass marshes serves to keep out larger bushes and trees, and releases nutrients from decaying plant matter more efficiently than decomposition.[44] Whereas in the wet season, dead plant matter and the tips of grasses and trees are burned, in the dry season the fire may be fed by organic peat and burn deeply, destroying root systems.[44] Fires are confined by existing water and rainfall. It takes approximately 225 years for one foot (0.30 m) of peat to develop, but in some locations the peat is less dense than it should be for the 5,000 years of the Everglades' existence.[45] Scientists indicate fire as the cause; it is also cited as the reason for the black color of Everglades muck. Layers of charcoal have been detected in the peat in portions of the Everglades that indicate the region endured severe fires for years at a time, although this trend seems to have abated since the last occurrence in 940 BC.[45]

Ecosystems

[edit]
Major landscape types in the Everglades before human action. Source: U.S. Geological Survey

Sawgrass marshes and sloughs

[edit]

Several ecosystems are present in the Everglades, and boundaries between them are subtle or absent. The primary feature of the Everglades is the sawgrass marsh. The iconic water and sawgrass combination in the shallow river 100 miles (160 km) long and 60 miles (97 km) wide that spans from Lake Okeechobee to Florida Bay is often referred to as the "true Everglades" or just "the Glades".[46][47] Prior to the first drainage attempts in 1905, the sheetflow occupied nearly a third of the lower Florida peninsula.[37] Sawgrass thrives in the slowly moving water, but may die in unusually deep floods if oxygen is unable to reach its roots. It is particularly vulnerable immediately after a fire.[48] The hydroperiod for the marsh is at least nine months, and can last longer.[49] Where sawgrass grows densely, few animals or other plants live, although alligators choose these locations for nesting. Where there is more room, periphyton grows.[50] Periphyton supports larval insects and amphibians, which in turn are consumed as food by birds, fish, and reptiles. It also absorbs calcium from water, which adds to the calcitic composition of the marl.[51]

Sloughs, or free-flowing channels of water, develop in between sawgrass prairies. Sloughs are about 3 feet (0.91 m) deeper than sawgrass marshes, and may stay flooded for at least 11 months out of the year and sometimes multiple years in a row.[52] Aquatic animals such as turtles, alligators, snakes, and fish thrive in sloughs; they usually feed on aquatic invertebrates.[53] Submerged and floating plants grow here, such as bladderwort (Utricularia), waterlily (Nymphaeaceae), and spatterdock (Nuphar lutea). Major sloughs in the Everglades system include the Shark River Slough flowing out to Florida Bay, Lostmans River Slough bordering The Big Cypress, and Taylor Slough in the eastern Everglades.

Wet prairies are slightly elevated like sawgrass marshes, but with greater plant diversity. The surface is covered in water only three to seven months of the year, and the water is, on average, shallow at only 4 inches (10 cm) deep.[54] When flooded, the marl can support a variety of water plants.[55] Solution holes, or deep pits where the limestone has worn away, may remain flooded even when the prairies are dry, and they support aquatic invertebrates such as crayfish and snails, and larval amphibians which feed young wading birds.[56] These regions tend to border between sloughs and sawgrass marshes.

Alligator in the Everglades

Alligators have created a niche in wet prairies. With their claws and snouts they dig at low spots and create ponds free of vegetation that remain submerged throughout the dry season. Alligator holes are integral to the survival of aquatic invertebrates, turtles, fish, small mammals, and birds during extended drought periods. The alligators then feed upon some of the animals that come to the hole.[57][58]

Tropical hardwood hammock

[edit]
In a tropical hardwood hammock, trees are very dense and diverse.

Small islands of trees growing on land raised between 1 and 3 feet (0.30 and 0.91 m) above sloughs and prairies are called tropical hardwood hammocks.[59] They may range from one (4,000 m2) to ten acres (40,000 m2) in area, and appear in freshwater sloughs, sawgrass prairies, or pineland. Hammocks are slightly elevated on limestone plateaus risen several inches above the surrounding peat, or they may grow on land that has been unharmed by deep peat fires. Hardwood hammocks exhibit a mixture of subtropical and hardwood trees, such as Southern live oak (Quercus virginiana), gumbo limbo (Bursera simaruba), royal palm (Roystonea), and bustic (Dipholis salicifolia) that grow in very dense clumps.[60] Near the base, sharp saw palmettos (Serenoa repens) flourish, making the hammocks very difficult for people to penetrate, though small mammals, reptiles and amphibians find these islands an ideal habitat. Water in sloughs flows around the islands, creating moats. Although some ecosystems are maintained and promoted by fire, hammocks may take decades or centuries to recover. The moats around the hammocks protect the trees.[61] The trees are limited in height by weather factors such as frost, lightning, and wind; the majority of trees in hammocks grow no higher than 55 feet (17 m).

Pineland

[edit]

Some of the driest land in the Everglades is pineland (also called pine rockland) ecosystem, located in the highest part of the Everglades with little to no hydroperiod. Some floors, however, may have flooded solution holes or puddles for a few months at a time. The most significant feature of the pineland is the single species of South Florida slash pine (Pinus elliottii). Pineland communities require fire to maintain them, and the trees have several adaptations that simultaneously promote and resist fire.[62] The sandy floor of the pine forest is covered with dry pine needles that are highly flammable. South Florida slash pines are insulated by their bark to protect them from heat. Fire eliminates competing vegetation on the forest floor, and opens pine cones to germinate seeds.[63] A period without significant fire can turn pineland into a hardwood hammock as larger trees overtake the slash pines.[64] The understory shrubs in pine rocklands are the fire-resistant saw palmetto (Serenoa repens), cabbage palm (Sabal palmetto), and West Indian lilac (Tetrazygia bicolor). The most diverse group of plants in the pine community are the herbs, of which there are two dozen species. These plants contain tubers and other mechanisms that allow them to sprout quickly after being charred.[65]

Prior to urban development of the South Florida region, pine rocklands covered approximately 161,660 acres (654.2 km2) in Miami-Dade County. Within Everglades National Park, 19,840 acres (80.3 km2) of pine forests are protected, but outside the park, 1,780 acres (7.2 km2) of pine communities remained as of 1990, averaging 12.1 acres (49,000 m2) in area.[62] The misunderstanding of the role of fire also played a part in the disappearance of pine forests in the area, as natural fires were put out and pine rocklands transitioned into hardwood hammocks. Prescribed fires occur in Everglades National Park in pine rocklands every three to seven years.[66]

A cross section of fresh water ecosystems in the Everglades, with relative average water depths

Cypress

[edit]
A pond in The Big Cypress

Cypress swamps can be found throughout the Everglades, but the largest covers most of Collier County. The Big Cypress Swamp is located to the west of the sawgrass prairies and sloughs, and it is commonly called "The Big Cypress".[67] The name refers to its area rather than the height or diameter of the trees; at its most conservative estimate, the swamp measures 1,200 square miles (3,100 km2), but the hydrologic boundary of The Big Cypress can be calculated at over 2,400 square miles (6,200 km2).[68] Most of The Big Cypress sits atop a bedrock covered by a thinner layer of limestone. The limestone underneath the Big Cypress contains quartz, which creates sandy soil that hosts a variety of vegetation different from what is found in other areas of the Everglades.[67] The basin for The Big Cypress receives on average 55 inches (140 cm) of water in the wet season.[69]

Although The Big Cypress is the largest growth of cypress swamps in South Florida, cypress swamps can be found near the Atlantic Coastal Ridge and between Lake Okeechobee and the Eastern flatwoods, as well as in sawgrass marshes. Cypresses are deciduous conifers that are uniquely adapted to thrive in flooded conditions, with buttressed trunks and root projections that protrude out of the water, called "knees".[70] Bald cypress trees grow in formations with the tallest and thickest trunks in the center, rooted in the deepest peat. As the peat thins out, cypresses grow smaller and thinner, giving the small forest the appearance of a dome from the outside.[71] They also grow in strands, slightly elevated on a ridge of limestone bordered on either side by sloughs.[72] Other hardwood trees can be found in cypress domes, such as red maple, swamp bay, and pop ash. If cypresses are removed, the hardwoods take over, and the ecosystem is recategorized as a mixed swamp forest.

Mangrove and Coastal prairie

[edit]
Red mangrove trees bordering a tidal estuary in the Everglades

Eventually the water from Lake Okeechobee and The Big Cypress makes its way to the ocean. Mangrove trees are well adapted to the transitional zone of brackish water where fresh and salt water meet.[73] The estuarine ecosystem of the Ten Thousand Islands, which is comprised almost completely of mangrove forests, covers almost 200,000 acres (810 km2).[74] In the wet season fresh water pours out into Florida Bay, and sawgrass begins to grow closer to the coastline. In the dry season, and particularly in extended periods of drought, the salt water creeps inland into the coastal prairie, an ecosystem that buffers the freshwater marshes by absorbing sea water. Mangrove trees begin to grow in fresh water ecosystems when the salt water goes far enough inland.[75]

There are three species of trees that are considered mangroves: red (Rhizophora mangle), black (Avicennia germinans), and white (Laguncularia racemosa), although all are from different families.[76] All grow in oxygen-poor soil, can survive drastic water level changes, and are tolerant of salt, brackish, and fresh water.[77] All three mangrove species are integral to coastline protection during severe storms. Red mangroves have the farthest-reaching roots, trapping sediments that help build coastlines after and between storms. All three types of trees absorb the energy of waves and storm surges. Everglades mangroves also serve as nurseries for crustaceans and fish, and rookeries for birds. The region supports Tortugas pink shrimp (Farfantepenaeus duorarum) and stone crab (Menippe mercenaria) industries;[78] between 80 and 90 percent of commercially harvested crustacean species in Florida's salt waters are born or spend time near the Everglades.[74][79]

Florida Bay

[edit]
A clump of mangroves in the distance, Florida Bay at Flamingo

Much of the coast and the inner estuaries are built of mangroves; there is no border between the coastal marshes and the bay. Thus the marine ecosystems in Florida Bay are considered to be a part of the Everglades watershed and one of the ecosystems connected to and affected by the Everglades as a whole. More than 800 square miles (2,100 km2) of Florida Bay is protected by Everglades National Park, representing the largest body of water in the park boundaries.[80] There are approximately 100 keys in Florida Bay, many of which are mangrove forests.[81] The fresh water coming into Florida Bay from the Everglades creates perfect conditions for vast beds of turtle grass and algae formations that are the foundation for animal life in the bay. Sea turtles and manatees eat the grass, while invertebrate animals, such as worms, clams and other mollusks eat the algae formations and microscopic plankton.[82] Female sea turtles return annually to nest on the shore, and manatees spend the winter months in the warmer water of the bay. Sea grasses also serve to stabilize the sea beds and protect shorelines from erosion by absorbing energy from waves.

History

[edit]

Native Americans

[edit]

Humans arrived in the Florida peninsula approximately 15,000 years ago. Paleo-Indians came to Florida probably following large game that included giant sloths, saber-toothed cats, and spectacled bears. They found an arid landscape that supported plants and animals adapted for desert conditions.[83] However, 6,500 years ago, climate changes brought a wetter landscape; large animals became extinct in Florida, and the Paleo-Indians slowly adapted and became the Archaic peoples. They conformed to the environmental changes, and created many tools with the various resources available.[84] During the Late Archaic period, the climate became wetter again, and approximately 3000 BCE the rise of water tables allowed an increase in population and cultural activity. Florida Indians developed into three distinct but similar cultures that were named for the bodies of water near where they were located: Okeechobee, Caloosahatchee, and Glades.[85]

Calusa and Tequesta

[edit]

From the Glades peoples, two major nations emerged in the area: the Calusa and the Tequesta. The Calusa was the largest and most powerful nation in South Florida. It controlled fifty villages located on Florida's west coast, around Lake Okeechobee, and on the Florida Keys. Most Calusa villages were located at the mouths of rivers or on key islands. The Calusa were hunter-gatherers who lived on small game, fish, turtles, alligators, shellfish, and various plants.[86] Most of their tools were made of bone or teeth, although sharpened reeds were also effective for hunting or war. Calusa weapons consisted of bows and arrows, atlatls, and spears. Canoes were used for transportation, and South Florida tribes often canoed through the Everglades, but rarely lived in them.[87] Canoe trips to Cuba were also common.[88]

Estimated numbers of Calusa at the beginning of the Spanish occupation ranged from 4,000 to 7,000.[89] The society declined in power and population; by 1697 their number was estimated to be about 1,000.[88] In the early 18th century, the Calusa came under attack from the Yamasee to the north. They asked the Spanish for refuge in Cuba, where almost 200 died of illness. Soon they were relocated again to the Florida Keys.[90]

Second in power and number to the Calusa in South Florida were the Tequesta. They occupied the southeastern portion of the lower peninsula in modern-day Dade and Broward counties. Like the Calusa, the Tequesta societies centered on the mouths of rivers. Their main village was probably on the Miami River or Little River. Spanish depictions of the Tequesta state that they were greatly feared by sailors, who suspected them of torturing and killing survivors of shipwrecks.[91] With an increasing European presence in south Florida, Native Americans from the Keys and other areas began increasing their trips to Cuba. Official permission for the immigration of Native Americans from the Florida Keys was granted by Cuban officials in 1704.[92] Spanish priests attempted to set up missions in 1743, but noted that the Tequesta were under assault from a neighboring tribe. When only 30 members were left, they were removed to Havana. A British surveyor in 1770 described multiple deserted villages in the region where the Tequesta lived.[93] Common descriptions of Native Americans in Florida by 1820 used only the term "Seminoles".[94]

Seminole

[edit]
Seminoles made their home in the Everglades.

Following the demise of the Calusa and Tequesta, Native Americans in southern Florida were referred to as "Spanish Indians" in the 1740s, probably due to their friendlier relations with Spain. The Creek invaded the Florida peninsula; they conquered and assimilated what was left of pre-Columbian societies into the Creek Confederacy. They were joined by remnant Indian groups and formed the Seminole, a new tribe, by ethnogenesis. The Seminole originally settled in the northern portion of the territory. In addition, free blacks and fugitive slaves made their way to Florida, where Spain had promised slaves freedom and arms if they converted to Catholicism and pledged loyalty to Spain. These African Americans gradually created communities near those of the Seminole, and became known as the Black Seminoles. The groups acted as allies.

In 1817, Andrew Jackson invaded Florida to hasten its annexation to the United States, in what became known as the First Seminole War. After Florida became a U.S. territory in 1821, conflicts between settlers and the Seminole increased as the former tried to acquire lands. The Second Seminole War lasted from 1835 to 1842, and afterward, the US forcibly removed about 3,000 Seminole and 800 Black Seminole to Indian Territory (now Oklahoma), west of the Mississippi River. Many others died in the war.[95] Conflict broke out again in the Third Seminole War from 1855 to 1859, when a few hundred Seminole fought off US forces from the swamps of the Everglades. The US finally decided to leave them alone, as they could not dislodge them even after this protracted and expensive warfare.

By 1913, the Seminole in the Everglades numbered no more than 325.[96] They made a living by hunting and trading with white settlers, and raised domesticated animals.[97] The Seminole made their villages in hardwood hammocks or pinelands, had diets of hominy and coontie roots, fish, turtles, venison, and small game.[96] Their villages were not large, due to the limited size of the hammocks. Between the end of the last Seminole War and 1930, the people lived in relative isolation from the majority culture.

The construction of the Tamiami Trail, beginning in 1928 and spanning the region from Tampa to Miami, altered their ways of life. Some began to work in local farms, ranches, and souvenir stands.[98] Some of the people who interacted more with European Americans began to move to reservations in the 1940s. These were their bases for reorganizing their government and they became federally recognized in 1957 as the Seminole Tribe of Florida.

People who kept more traditional ways had settlements along the Tamiami Trail and tended to speak the Mikasuki language. They later were federally recognized in 1962 as the Miccosukee Tribe of Indians of Florida. As metropolitan areas in South Florida began to grow, the two groups were closely associated with the Everglades. They struggled to maintain privacy while serving as tourist attractions. They earned money by wrestling alligators and selling craftworks.[99] As of 2008, the Seminole Tribe of Florida had five reservations, and the lands of the Miccosukee Tribe of Indians were collectively considered a sixth reservation. The two tribes have each developed casino gaming on some of their properties to generate revenue for support, services and economic development.[100]

Exploration

[edit]
Map of the Everglades in 1856: Military action during the Seminole Wars improved understanding of the features of the Everglades.

The military penetration of southern Florida offered the opportunity to map a poorly understood and largely unknown part of the country. An 1840 expedition into the Everglades offered the first printed account for the general public to read about the Everglades. The anonymous writer described the terrain the party was crossing:

No country that I have ever heard of bears any resemblance to it; it seems like a vast sea filled with grass and green trees, and expressly intended as a retreat for the rascally Indian, from which the white man would never seek to drive them.[101]

The land seemed to inspire extreme reactions of both wonder or hatred. During the Second Seminole War an army surgeon wrote, "It is in fact a most hideous region to live in, a perfect paradise for Indians, alligators, serpents, frogs, and every other kind of loathsome reptile."[102]

A survey team led by railroad executive James Edmundson Ingraham explored the area in 1892.[103] In 1897, explorer Hugh Willoughby spent eight days canoeing with a party from the mouth of the Harney River to the Miami River. He sent his observations to the New Orleans Times-Democrat. Willoughby described the water as healthy and wholesome, with numerous springs, and 10,000 alligators "more or less" in Lake Okeechobee. The party encountered thousands of birds near the Shark River, "killing hundreds, but they continued to return".[104] Willoughby pointed out that much of the rest of the country had been explored and mapped except for this part of Florida, writing, "(w)e have a tract of land one hundred and thirty miles long and seventy miles wide that is as much unknown to the white man as the heart of Africa."[105]

Drainage

[edit]

A national push for expansion and progress in the United States occurred in the later part of the 19th century, which stimulated interest in draining the Everglades for agricultural use. According to historians, "From the middle of the nineteenth century to the middle of the twentieth century, the United States went through a period in which wetland removal was not questioned. Indeed, it was considered the proper thing to do."[106] Draining the Everglades was suggested as early as 1837,[5] and a resolution in Congress was passed in 1842 that prompted Secretary of Treasury Robert J. Walker to request those with experience in the Everglades to give their opinion on the possibility of drainage. Many officers who had served in the Seminole Wars favored the idea.[5] In 1850 Congress passed a law that gave several states wetlands within their state boundaries. The Swamp and Overflowed Lands Act ensured that the state would be responsible for funding the attempts at developing wetlands into farmlands.[107] Florida quickly formed a committee to consolidate grants to pay for any attempts, though the Civil War and Reconstruction halted progress until after 1877.

Hamilton Disston's land sale notice

After the Civil War, a state agency called the Internal Improvement Fund (IIF), whose purpose was to improve Florida's roads, canals, and rail lines, was discovered to be deeply in debt. The IIF found a Pennsylvania real estate developer named Hamilton Disston interested in implementing plans to drain the land for agriculture. Disston purchased 4,000,000 acres (16,000 km2) of land for $1 million in 1881,[108] and he began constructing canals near St. Cloud. At first, the canals seemed to work in lowering the water levels in the wetlands surrounding the rivers.[109] They were effective in lowering the groundwater, but it became apparent that their capacity was insufficient for the wet season.[110] Although Disston's canals did not drain well, his purchase primed the economy of Florida. It made news and attracted tourists and land buyers. Within four years property values doubled, and the population increased significantly.[108]

The IIF was able to invest in development projects due to Disston's purchase, and an opportunity to improve transportation arose when oil tycoon Henry Flagler began purchasing land and building rail lines along the east coast of Florida, as far south as Palm Beach in 1893.[111] Along the way he built resort hotels, transforming territorial outposts into tourist destinations. The land bordering the rail lines was developed as citrus farms.[112] By 1896 the rail line had been extended to Biscayne Bay.[113] Three months after the first train had arrived, the residents of Miami voted to incorporate the town. Miami became a prime destination for extremely wealthy people after the Royal Palm Hotel was opened.[114]

During the 1904 gubernatorial race, the strongest candidate, Napoleon Bonaparte Broward, a populist Democrat from Duval County, promoted draining the Everglades. He called the future of South Florida the "Empire of the Everglades". Soon after his successful election, he began work to "drain that abominable pestilence-ridden swamp",[115] and pushed the Florida legislature to form a group of commissioners to oversee reclamation of flooded lands. In 1907 they established the Everglades Drainage District and began to study how to build the most effective canals, and how to fund them.[5] Governor Broward ran for the U.S. Senate in 1908 but lost. Broward was paid by land developer Richard J. Bolles to tour the state to promote drainage. Elected to the Senate in 1910, Broward died before he could take office. Land in the Everglades was being sold for $15 an acre a month after Broward died.[116] Meanwhile, Henry Flagler continued to build railway stations at towns as soon as the populations warranted them.[113]

Growth of urban areas

[edit]
A canal lock in the Everglades Drainage District around 1915

With the construction of canals, newly reclaimed Everglades land was promoted throughout the United States. Land developers sold 20,000 lots in a few months in 1912. Advertisements promised within eight weeks of arrival, a farmer could be making a living, although for many it took at least two months to clear the land. Some tried burning off the sawgrass or other vegetation, only to learn that the peat continued to burn. Animals and tractors used for plowing got mired in the muck and were useless. When the muck dried, it turned to a fine black powder and created dust storms.[117] Although initially crops sprouted quickly and lushly, they just as quickly wilted and died, seemingly without reason.[118]

The increasing population in towns near the Everglades hunted in the area. Raccoons and otters were the most widely hunted for their skins. Hunting often went unchecked; in one trip, a Lake Okeechobee hunter killed 250 alligators and 172 otters.[119] Water birds were a particular target of plume hunting. Bird feathers were used in women's hats in the late 19th and early 20th centuries.

In 1886, 5 million birds were estimated to be killed for their feathers.[120] They were shot usually in the spring, when their feathers were colored for mating and nesting. The plumes, or aigrettes, as they were called in the millinery business, sold for $32 an ounce in 1915—the price of gold.[119] Millinery was a $17 million a year industry[121] that motivated plume harvesters to lay in watch of nests of egrets and many colored birds during the nesting season, shoot the parents with small-bore rifles, and leave the chicks to starve.[119] Plumes from Everglades wading birds could be found in Havana, New York City, London, and Paris. Hunters could collect plumes from a hundred birds on a good day.[122]

Rum-runners used the Everglades as a hiding spot during Prohibition; it was so vast there were never enough law enforcement officers to patrol it.[123] The arrival of the railroad, and the discovery that adding trace elements like copper was the remedy for crops sprouting and dying quickly, soon created a population boom. New towns such as Moore Haven, Clewiston, and Belle Glade sprouted like the crops.[5] Sugarcane became the primary crop grown in South Florida. Miami experienced a second real estate boom that earned a developer in Coral Gables $150 million. Undeveloped land north of Miami sold for $30,600 an acre.[124] In 1925, Miami newspapers published editions weighing over 7 pounds (3.2 kg), most of it in real estate advertising.[125] Waterfront property was the most highly valued. Mangrove trees were cut down and replaced with palm trees to improve the view. Acres of South Florida slash pine were cleared. Some of the pine was for lumber, but most of the pine forests in Dade County were cleared for development.[62]

Flood control

[edit]
A sign advertising the completion of the Herbert Hoover Dike

Two catastrophic hurricanes in 1926 and 1928 caused Lake Okeechobee to breach its levees, killing thousands of people. The government began to focus on the control of floods rather than drainage. The Okeechobee Flood Control District was created in 1929, financed by both state and federal funds. President Herbert Hoover toured the towns affected by the 1928 Okeechobee Hurricane and ordered the Army Corps of Engineers to assist the communities surrounding the lake.[126] Between 1930 and 1937 a dike 66 miles (106 km) long was built around the southern edge of the lake. Control of the Hoover Dike and the waters of Lake Okeechobee was delegated to federal powers: the United States declared legal limits of the lake to between 14 and 17 feet (4.3 and 5.2 m).[105] A massive canal was also constructed 80 feet (24 m) wide and 6 feet (1.8 m) deep through the Caloosahatchee River; whenever the lake rose too high, the excess water left through the canal.[105] More than $20 million was spent on the entire project. Sugarcane production soared after the dike and canal were built. The populations of the small towns surrounding the lake jumped from 3,000 to 9,000 after World War II.[127]

Immediately, the effects of the Hoover Dike were seen. An extended drought occurred in the 1930s; with the wall preventing water from leaving Lake Okeechobee and canals and ditches removing other water, the Everglades became parched. Peat turned to dust. Salt ocean water intruded into Miami's wells; when the city brought in an expert to explain why, he discovered that the water in the Everglades was the area's groundwater—here, it appeared on the surface.[128] In 1939, a million acres (4,000 km2) of Everglades burned, and the black clouds of peat and sawgrass fires hung over Miami.[129] Scientists who took soil samples before draining did not take into account that the organic composition of peat and muck in the Everglades make it prone to soil subsidence when it becomes dry. Naturally occurring bacteria in Everglades peat and muck assist with the process of decomposition under water, which is generally very slow, partially due to the low levels of dissolved oxygen. When water levels became so low that peat and muck were at the surface, the bacteria interacted with much higher levels of oxygen in the air, rapidly breaking down the soil. In some places, homes had to be moved to stilts and 8 feet (2.4 m) of soil was lost.[43]

Everglades National Park

[edit]
President Harry Truman dedicating Everglades National Park on December 6, 1947

The idea of a national park for the Everglades was pitched in 1928, when a Miami land developer named Ernest F. Coe established the Everglades Tropical National Park Association. It had enough support to be declared a national park by Congress in 1934. It took another 13 years to be dedicated on December 6, 1947.[130] One month before the dedication of the park, a former editor from The Miami Herald and freelance writer named Marjory Stoneman Douglas released her first book titled The Everglades: River of Grass. After researching the region for five years, she described the history and ecology of South Florida in great detail. She characterized the Everglades as a river instead of a stagnant swamp.[131] The last chapter was titled "The Eleventh Hour" and warned that the Everglades were dying, although it could be reversed.[132]

Central and Southern Florida Flood Control Project

[edit]

The same year the park was dedicated, two hurricanes and the wet season caused 100 inches (250 cm) to fall on South Florida. Although there were no human casualties, agricultural interests lost approximately $59 million (equivalent to $780 million in 2024).[133] In 1948, Congress approved the Central and Southern Florida Project for Flood Control and Other Purposes (C&SF), which divided the Everglades into basins. In the northern Everglades were Water Conservation Areas (WCAs), and the Everglades Agricultural Area (EAA) bordering to the south of Lake Okeechobee. In the southern Everglades was Everglades National Park. Levees and pumping stations bordered each WCA, and released water in dryer times or removed it and pumped it to the ocean in times of flood. The WCAs took up approximately 37 percent of the original Everglades.[134] The C&SF constructed over 1,000 miles (1,600 km) of canals, and hundreds of pumping stations and levees within three decades. During the 1950s and 1960s the Miami metropolitan area grew four times as fast as the rest of the nation. Between 1940 and 1965, 6 million people moved to South Florida: 1,000 people moved to Miami every week.[135] Developed areas between the mid-1950s and the late 1960s quadrupled. Much of the water reclaimed from the Everglades was sent to newly developed areas.[136]

Everglades Agricultural Area

[edit]
A 2003 U.S. Geological Survey photo showing the border between Water Conservation Area 3 (bottom) with water, and Everglades National Park, dry (top)

The C&SF established 470,000 acres (1,900 km2) for the Everglades Agricultural Area—27 percent of the Everglades prior to development.[137] In the late 1920s, agricultural experiments indicated that adding large amounts of manganese sulfate to Everglades muck produced a profitable harvest for vegetables.[138] The primary cash crop in the EAA is sugarcane, though sod, beans, lettuce, celery, and rice are also grown. Fields in the EAA are typically 40 acres (160,000 m2), bordered by canals on two sides, that are connected to larger canals where water is pumped in or out depending on the needs of the crops.[139] The fertilizers used on vegetables, along with high concentrations of nitrogen and phosphorus that are the byproduct of decayed soil necessary for sugarcane production, were pumped into WCAs south of the EAA. The introduction of large amounts of these chemicals provided opportunities for exotic plants to take hold in the Everglades.[140] One of the defining characteristics of natural Everglades ecology is its ability to support itself in a nutrient-poor environment, and the introduction of fertilizers began to alter the plant life in the region.[141]

Jetport proposition

[edit]

A turning point came for development in the Everglades at the proposal in the late 1960s for an expanded airport, after Miami International Airport outgrew its capacities. The new jetport was planned to be larger than O'Hare, Dulles, JFK, and LAX airports combined,[citation needed] and the chosen location was 6 miles (9.7 km) north of Everglades National Park. The first sentence of the U.S. Department of Interior study of the environmental impact of the jetport read, "Development of the proposed jetport and its attendant facilities ... will inexorably destroy the south Florida ecosystem and thus the Everglades National Park".[142] When studies indicated the proposed jetport would create 4,000,000 US gallons (15,000,000 L) of raw sewage a day and 10,000 short tons (9,100 t) of jet engine pollutants a year, the project met staunch opposition. The New York Times called it a "blueprint for disaster",[143] and Wisconsin senator Gaylord Nelson wrote to President Richard Nixon voicing his opposition: "It is a test of whether or not we are really committed in this country to protecting our environment."[144] Governor Claude Kirk withdrew his support for the project, and Marjory Stoneman Douglas was persuaded at 79 years old to go on tour to give hundreds of speeches against it. Nixon instead proposed Big Cypress National Preserve, announcing it in the Special Message to the Congress Outlining the 1972 Environmental Program.[145] Although construction of only one runway was completed, the remains of the Everglades Jetport was later opened as the Dade-Collier Training and Transition Airport and is sometimes used as an aviation training facility.

Restoration

[edit]

The International Union for Conservation of Nature (IUCN) World Heritage Outlook cited the Everglades National Park 2020 Conservation Outlook as "Critical". Assessment of current trends were concluded to be "deteriorating" with "very high threat" to the overall health of the ecosystem. Unfortunately, some ecological features now lost cannot be restored as they were initially developed over decades to centuries.[146] The surviving ecological features are of vital importance to protect due to their essential support of the state of Florida and their unique properties, unknown elsewhere in the world and are of invaluable consequence to multiple fields of study.

Major contributors to this decline include water quality (nutrient pollution), quantity (reduced water flow), distribution, and timing; invasive species; climate change (sea-level rise, etc.); ocean acidification; and hurricanes. Other significant threats to the restoration and conservation of the Everglades are lagging logistic and legislative action. Restoration projects in other areas of Florida (i.e. Tamami Trail Next Steps, water storage and treatment south of Lake Okeechobee, etc.), as well as decompartmentalization of the varying jurisdictions and regional water quality/quantity measures which are upstream of the ecosystem, have not received adequate attention, but are essential to prevent further loss.[146]

While some Everglades Restoration projects have been completed, critical plans remain incomplete. Further, pre-CERP components of current plans overestimated the hydrologic and ecologic benefits of these plans, and restoration projects to be complete by 2027 that address these "benefit setbacks" lack timely funding.[146]

Recent changes in internal site policies have been lauded as showing promising improvement, including improved consistency in the management of park visitor activities, efforts to deal with invasive species, improving prescribed fire activities, and increasing financing opportunities for internal park projects. However, although the site itself is increasing work to deal with salient issues, support at the local, state, and federal level have not been in proportion to the critical nature of conservation efforts.[146]

Kissimmee River

[edit]

The Central and Southern Florida Flood Control Project's final construction project was straightening the Kissimmee River, a meandering 90-mile-long (140 km) river that was drained to make way for grazing land and agriculture. The C&SF started building the C-38 canal in 1962 and the effects were seen almost immediately. Waterfowl, wading birds, and fish disappeared, prompting conservationists and sport fishers to demand the region be restored before the canal was finished in 1971.[147] In general, C&SF projects had been criticized for being temporary fixes that ignored future consequences, costing billions of dollars with no end in sight.[148] After Governor Bob Graham initiated the Save Our Everglades campaign in 1983, the first section of the canal was backfilled in 1986. Graham announced that by 2000 the Everglades would be restored as closely as possible to its pre-drainage state.[149] The Kissimmee River Restoration project was approved by Congress in 1992. It is estimated that it will cost $578 million to convert only 22 miles (35 km) of the canal. The entire project was to be complete by 2011,[150] yet as of 2017, the project is "more than halfway complete" and the new completion date is 2020.[151]

Water quality

[edit]
Warnings are placed in Everglades National Park to dissuade people from eating fish due to high mercury content. This warning explicitly mentions bass.

Further problems with the environment arose when a vast algal bloom appeared in one-fifth of Lake Okeechobee in 1986, the same year cattails were discovered overtaking sawgrass marshes in Loxahatchee National Wildlife Refuge. Scientists discovered that phosphorus, used as a fertilizer in the EAA, was flushed into canals and pumped back into the lake.[152] When the lake drained, the phosphorus entered the water in the marshes, changing the nutrient levels. It kept periphyton from forming marl, one of two soils in the Everglades. The arrival of phosphorus allowed cattails to spread quickly. The cattails grew in dense mats—too thick for birds or alligators to nest in. It also dissolved oxygen in the peat, promoted algae, and prohibited the growth of native invertebrates on the bottom of the food chain.[153]

At the same time mercury was found in local fish at such high levels that consumption warnings were posted for fishermen. A Florida panther was found dead with levels of mercury high enough to kill a human.[154] Scientists found that power plants and incinerators using fossil fuels were expelling mercury into the atmosphere, and it fell as rain or dust during droughts. The naturally occurring bacteria that reduce sulfur in the Everglades ecosystem were transforming the mercury into methylmercury, and it was bioaccumulating through the food chain.[154] Stricter emissions standards helped lower mercury coming from power plants and incinerators, which in turn lowered mercury levels found in animals, though they continue to be a concern.[154]

In recent studies of the water quality, the studies showed how the different cycles throughout the year in Lake Okeechobee affect the cyanobacteria bloom, which include toxin-producing Microcystis aeruginosa that cause microcystin, a strong kind of hepatotoxin that affects both humans and animals.[155] The studied showcased the movement of diurnal cycles of atmospheric forcing and diel vertical migration this concluded that during the summer cyanobacteria concentrated in the northern and central and a concentration in the western lake during the spring and fall.[155] The flow of the lake carries cyanobacteria and other phytoplankton cells into estuaries; this can lead to water quality deterioration.[155]

The Everglades Forever Act, introduced by Governor Lawton Chiles in 1994, was an attempt to legislate the lowering of phosphorus in Everglades waterways. The act put the South Florida Water Management District (SFWMD) and the Florida Department of Environmental Protection (DEP) in charge of testing and enforcing low phosphorus levels: 10 parts per billion (ppb) (down from 500 ppb in the 1980s).[156] The SFWMD built Stormwater Treatment Areas (STAs) near sugarcane fields where water leaving the EAA flows into ponds lined with lime rock and layers of peat and calcareous periphyton. Testing has shown this method to be more effective than previously anticipated, bringing levels from 80 ppb to 10 ppb.[157]

Invasive species

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Climbing ferns overtake cypress trees in the Everglades. The ferns act as "fire ladders" that can destroy trees that would otherwise survive fires.

As a center for trade and travel between the U.S., the Caribbean, and South America, South Florida is especially vulnerable to invasive species, or species of plants and animals that adapt aggressively to conditions in the Everglades, allowing them to reproduce faster and grow larger than they would naturally in their native environments. Approximately 26% of all species of fish, reptiles, birds, and mammals in South Florida are exotic—more than in any other part of the U.S.—and the region hosts one of the highest numbers of exotic plant species in the world.[158] Controlling invasive species in 1,700,000 acres (6,900 km2) of infested land in South Florida costs authorities about $500 million a year.[159]

The Everglades hosts 1,392 exotic plant species actively reproducing in the region, outnumbering the 1,301 species considered native to South Florida.[160] The melaleuca tree (Melaleuca quinquenervia) takes water in greater amounts than other trees. Melaleucas grow taller and more densely in the Everglades than in their native Australia, making them unsuitable as nesting areas for birds with wide wingspans.[161] They also choke out native vegetation. More than $2 million has been spent on keeping them out of Everglades National Park.[162]

Brazilian pepper, or Florida holly (Schinus terebinthifolius), has also wreaked havoc on the Everglades, exhibiting a tendency to spread rapidly and to crowd out native species of plants as well as to create inhospitable environments for native animals. It is especially difficult to eradicate and is readily propagated by birds, which eat its small red berries.[163] The Brazilian pepper problem is not exclusive to the Everglades; neither is the water hyacinth (Eichhornia crassipes), which is a widespread problem in Florida's waterways, a major threat to endemic species, and is difficult and costly to eradicate. The Old World climbing fern (Lygodium microphyllum) may be causing the most harm to restoration as it blankets areas thickly, making it impossible for animals to pass through. It also climbs up trees and creates "fire ladders", allowing parts of the trees to burn that would otherwise remain unharmed.[164]

Many pets have escaped or been released into the Everglades from the surrounding urban areas. Some find the conditions quite favorable and have established self-sustaining populations, competing for food and space with native animals. Many tropical fish have been released, but blue tilapias (Oreochromis aureus) cause damage to shallow waterways by creating large nests and consuming aquatic plants that protect native young fish.[165]

Native to southern Asia, the Burmese python (Python molurus bivittatus) is a relatively new invasive species in the Everglades. This species can grow up to 20 feet (6.1 m) long, and they compete with alligators for the top of the food chain. Florida wildlife officials speculate that escaped pythons have begun reproducing in an environment for which they are well-suited.[166][167] In 2017 The South Florida Water Management District implemented the Python Elimination program, hoping to encourage the public to participate in the removal of the snakes by placing a cash reward per foot of python captured and euthanized with an additional wage pay and $200 per active nest found.[168] In Everglades National Park alone, agents removed more than 2,000 Burmese pythons from the park as of 2017.[169] Federal authorities banned four species of exotic snakes, including the Burmese python, in 2012.[170] The pythons are believed to be responsible for drastic decreases in the populations of some mammals within the park.[171] In a 2015 study by the United States Geological Survey, Florida Fish and Wildlife Conservation Commission, and the University of Florida, 95 adult marsh rabbits were released and tracked in areas known to have invasive python populations. 11 months later, it was found that 77% of the rabbits that fell victim to predation, was due to pythons.[172] Relationships like these are believed to be a reason for declining native predator populations such as the Florida Panther that has less than 500 remaining individuals in the wild.[173]

Comprehensive Everglades Restoration Plan

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Although scientists made headway in decreasing mercury and phosphorus levels in water, the natural environment of South Florida continued to decline in the 1990s, and life in nearby cities reflected this downturn. To address the deterioration of the Miami metropolitan area, Governor Lawton Chiles commissioned a report on the sustainability of the area. In 1995, Chiles published the commission's findings in a report that related the degradation of the Everglades ecosystems to the lower quality of life in urban areas. The report noted past environmental abuses that brought the state to a position to make a decision. Not acting to improve the South Florida ecosystem, the report predicted, would inevitably cause further and intolerable deterioration that would harm local tourism by 12,000 jobs and $200 million annually, and commercial fishing by 3,300 jobs and $52 million annually.[174] Urban areas had grown beyond their capacities to sustain themselves. Crowded cities were facing problems such as high crime rates, traffic jams, severely overcrowded schools, and overtaxed public services; the report noted that water shortages were ironic, given the 53 inches (130 cm) of rain the region received annually.[174]

In 1999, an evaluation of the C&SF was submitted to Congress as part of the Water Development Act of 1992. The seven-year report, called the "Restudy", cited indicators of harm to the ecosystem: a 50 percent reduction in the original Everglades, diminished water storage, harmful timing of water releases from canals and pumping stations, an 85 to 90 percent decrease in wading bird populations over the past 50 years, and the decline of output from commercial fisheries. Bodies of water including Lake Okeechobee, the Caloosahatchee River, St. Lucie estuary, Lake Worth Lagoon, Biscayne Bay, Florida Bay and the Everglades reflected drastic water level changes, hypersalinity, and dramatic changes in marine and freshwater ecosystems. The Restudy noted the overall decline in water quality over the past 50 years was due to loss of wetlands that act as filters for polluted water.[175] It predicted that without intervention the entire South Florida ecosystem would deteriorate. Water shortages would become common and some cities would have annual water restrictions.[176]

Planned water recovery and storage implementation using CERP strategies

The Restudy came with a plan to stop the declining environmental quality, and this proposal was to be the most expensive and comprehensive ecological repair project in history.[177] The Comprehensive Everglades Restoration Plan (CERP) proposed more than 60 construction projects over 30 years to store water that was being flushed into the ocean, in reservoirs, underground aquifers, and abandoned quarries; add more Stormwater Treatment Areas to filter water that flowed into the lower Everglades; regulate water released from pumping stations into local waterways and improve water released to Everglades National Park and Water Conservation Areas; remove barriers to sheetflow by raising the Tamiami Trail and destroying the Miami Canal, and reuse wastewater for urban areas.[178] The cost estimate for the entire plan was $7.8 billion, and in a bipartisan show of cooperation, CERP was voted through Congress with an overwhelming margin. It was signed by President Bill Clinton on December 11, 2000.[179]

Since its signing, the State of Florida reports that it has spent more than $2 billion on the various projects. More than 36,000 acres (150 km2) of Stormwater Treatment Areas have been constructed to filter 2,500 short tons (2,300 t) of phosphorus from Everglades waters. An STA spanning 17,000 acres (69 km2) was constructed in 2004, making it the largest manmade wetland in the world. Fifty-five percent of the land necessary to acquire for restoration has been purchased by the State of Florida, totaling 210,167 acres (850.52 km2). A plan to hasten the construction and funding of projects was put into place, named "Acceler8", spurring the start of six of eight large construction projects, including that of three large reservoirs.[180] However, federal funds have not been forthcoming; CERP was signed when the U.S. government had a budget surplus, but since then deficits have renewed, and two of CERP's major supporters in Congress retired. According to a story in The New York Times, state officials say the restoration is lost in a maze of "federal bureaucracy, a victim of 'analysis paralysis'".[181] CERP still remains controversial as the projects slated for Acceler8, environmental activists note, are those that benefit urban areas, and regions in the Everglades in desperate need of water are still being neglected, suggesting that water is being diverted to make room for more people in an already overtaxed environment.[182]

Airboating has become a popular ecotourism attraction in the Everglades.

A series of biennial reports from the U.S. National Research Council have reviewed the progress of CERP. The fourth report in the series, released in 2012, found that little progress has been made in restoring the core of the remaining Everglades ecosystem; instead, most project construction so far has occurred along its periphery.[183] The report noted that to reverse ongoing ecosystem declines, it will be necessary to expedite restoration projects that target the central Everglades, and to improve both the quality and quantity of the water in the ecosystem.[184] To better understand the potential implications of the current slow pace of progress, the report assessed the current status of ten Everglades ecosystem attributes, including phosphorus loads, peat depth, and populations of snail kites, birds of prey that are endangered in South Florida. Most attributes received grades ranging from C (degraded) to D (significantly degraded), but the snail kite received a grade of F (near irreversible damage). The report also assessed the future trajectory of each ecosystem attribute under three restoration scenarios: improved water quality, improved hydrology, and improvements to both water quality and hydrology, which helped highlight the urgency of restoration actions to benefit a wide range of ecosystem attributes and demonstrate the cost of inaction.[184] Overall, the report concluded that substantial near-term progress to address both water quality and hydrology in the central Everglades is needed to reverse ongoing degradation before it is too late.

Future of the Everglades

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In 2008, the State of Florida agreed to buy U.S. Sugar and all of its manufacturing and production facilities for an estimated $1.7 billion.[185] Florida officials indicated they intended to allow U.S. Sugar to process for six more years before dismissing its employees and dismantling the plant. The area, which includes 187,000 acres (760 km2) of land, would then be rehabilitated and water flow from Lake Okeechobee would be restored.[185] In November 2008, the agreement was revised to offer $1.34 billion, allowing sugar mills in Clewiston to remain in production.[186] Critics of the revised plan say that it ensures sugarcane will be grown in the Everglades for at least another decade.[187] Further research is being done to address the continuing production of sugarcane in the Everglades to minimize phosphorus runoff.[188]

Everglades restoration received $96 million of the American Recovery and Reinvestment Act of 2009.[189] As a result of the stimulus package, a mile-long (1.6 km) bridge to replace the Tamiami Trail, a road that borders Everglades National Park to the north and has blocked water from reaching the southern Everglades, was begun by the Army Corps of Engineers in December 2009. The next month work began to reconstruct the C-111 canal, east of the park that historically diverted water into Florida Bay.[190][191] Governor Charlie Crist announced the same month that $50 million of state funds would be earmarked for Everglades restoration.[192] In May 2010, 5.5 miles (8.9 km) of bridges were proposed to be added to the Tamiami Trail.[193]

Plane crashes

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At least three airplanes have crashed in the Everglades:

See also

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References

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Bibliography

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[edit]
Revisions and contributorsEdit on WikipediaRead on Wikipedia
from Grokipedia
The Everglades is a subtropical wetland ecosystem spanning approximately 2 million acres across southern Florida, forming a unique mosaic of sawgrass marshes, cypress sloughs, pine flatwoods, hardwood hammocks, and mangrove estuaries.[1] This vast region, often described as a "river of grass," relies on slow-moving sheet flow of freshwater originating from Lake Okeechobee and extending southward over 100 miles to Florida Bay, sustained by seasonal rainfall and porous limestone bedrock that underlies the shallow waters.[2] Historically covering around 11,000 square miles, the Everglades has been diminished by more than half through extensive canal dredging, levee construction, and land reclamation for agriculture and urban expansion starting in the late 19th century, which disrupted natural hydrologic patterns and introduced ecological imbalances such as nutrient enrichment and habitat fragmentation.[3] The ecosystem supports exceptional biodiversity, harboring over 350 bird species, 300 freshwater and 90 saltwater fish species, and numerous endemic reptiles, mammals, and invertebrates, including threatened icons like the Florida panther and American crocodile, though populations have declined due to altered water flows, invasive species proliferation, and contamination from agricultural runoff.[4] Designated as a UNESCO World Heritage Site, International Biosphere Reserve, and Wetland of International Importance, the Everglades exemplifies causal dependencies on precise hydrologic regimes, where deviations—such as reduced freshwater delivery exacerbating saltwater intrusion—have precipitated cascading trophic shifts, underscoring the need for restoration initiatives like the Comprehensive Everglades Restoration Plan to reinstate pre-drainage dynamics.[5]

Physical Geography

Geology and Formation

The Everglades rest on a foundation of carbonate bedrock primarily composed of limestone formations developed over millions of years through marine deposition and diagenesis. The dominant surface rock is the Miami Limestone, a Pleistocene oolitic limestone formed approximately 130,000 years ago during the Sangamonian interglacial period when higher sea levels created shallow marine environments conducive to ooid formation and cementation.[6] This unit overlies older Miocene to Pliocene formations such as the Tamiami Formation, which consists of fossiliferous carbonates and siliciclastics deposited in marine settings.[7] Beneath these lies the Hawthorn Group and other Tertiary strata, reflecting Florida's history as a stable carbonate platform accumulating sediments since the late Eocene.[8] South Florida's low-relief topography and karst features, including solution pits and an uneven limestone floor, result from prolonged subaerial exposure and dissolution during glacial lowstands, particularly the last glacial maximum around 18,000 years ago when sea levels dropped over 100 meters below present.[6] Post-glacial sea-level rise, stabilizing around 5,000 to 6,000 years before present, flooded coastal margins but preserved an inland freshwater basin bounded by the Atlantic Coastal Ridge to the east and higher interior highlands to the north and west.[3] This basin, with elevations rarely exceeding 2 meters above sea level, facilitated the slow southward sheet flow of freshwater from Lake Okeechobee, promoting organic sediment accumulation rather than mineral deposition.[2] The contemporary Everglades landscape emerged through autogenic processes in this limestone depression, where prolonged inundation led to peat buildup from decaying vegetation, reaching thicknesses up to 1.5 meters in some sloughs while marl layers formed in slightly more mineral-influenced areas.[6] These Holocene sediments overlie the karstic bedrock, concealing it except in exposed "rockland" areas, and their formation depended on the impermeability of underlying clays and the flatness imparted by prior marine planation.[3] Ongoing dissolution and compaction continue to shape microtopography, creating tree islands on slight elevations and sloughs in depressions.[2]

Hydrology and Water Flow

The Everglades' hydrology features a vast, shallow sheet flow of freshwater extending southward from Lake Okeechobee across a low-gradient landscape to Florida Bay, historically covering about 11,000 square miles.[1] This diffuse flow, often termed a "river of grass," moves as a broad, unchannelized expanse up to 48 kilometers wide, with water depths averaging 15 cm to 1 m, typically concealed by dense vegetation.[9] This slow sheet flow maintained clear waters by allowing low-phosphorus rainwater to trickle over the porous limestone bedrock, preventing dense floating plant growth and resulting in vast sawgrass prairies with clear sloughs.[10] The system's primary water source is regional rainfall, augmented by seasonal overflows from Lake Okeechobee fed by the Kissimmee River watershed, while evapotranspiration exerts a counterbalancing influence on water levels.[2] [11] The subtle topographic gradient, less than 4.5 cm per km over roughly 160 km, drives this slow surface flow at velocities around 34 m per day in sloughs, with even lower rates across the prairie due to vegetative drag and microtopography.[9] [12] Porous oolitic limestone bedrock, riddled with karst solution holes and conduits, permits significant groundwater seepage and exchange, contributing to the overall hydrologic connectivity while solution holes trap organic matter and influence local retention.[2] [13] In the natural regime, seasonal wet periods from June to October elevate water levels, promoting southward propagation, whereas dry seasons from November to May lead to gradual recession, maintaining a dynamic balance essential for wetland persistence.[14] Contemporary hydrology deviates markedly from this pattern due to an extensive network of canals, levees, and structures—initially constructed for flood control and agriculture—that channelize flow, reduce sheet flow extent, and regulate releases from Lake Okeechobee, often diverting water eastward and westward rather than southward.[2] This alteration has shortened hydrologic residence times, diminished natural pulsing, and exacerbated issues like hypersalinity in Florida Bay during low-flow periods.[15] Restoration efforts aim to reestablish more natural sheet flow dynamics through initiatives like removing barriers and decommissioning canals to mimic pre-drainage conditions.[1]

Climate and Weather Patterns

The Everglades exhibit a humid subtropical climate influenced by its position on the Florida peninsula, transitioning from temperate to tropical zones, with warm, humid conditions year-round moderated by marine influences from the Gulf of Mexico and Atlantic Ocean. Average annual temperatures range from lows of 54°F (12°C) in winter to highs of 92°F (33°C) in summer, with minimal seasonal variation of less than 20°F (11°C) due to the region's latitude and oceanic proximity. Annual precipitation averages 60 inches (152 cm), predominantly occurring during the wet season from May to October, driven by convective thunderstorms, sea breezes, and tropical disturbances.[16][17][18] The wet season, spanning mid-May to November, features daily afternoon thunderstorms fueled by high humidity exceeding 90% and temperatures averaging 90°F (32°C), leading to widespread flooding across the low-relief landscape and supporting peak hydrologic flows. In contrast, the dry season from December to April brings milder conditions with highs around 77°F (25°C), lows near 60°F (16°C), and occasional cold fronts dropping temperatures into the 40s°F (4–9°C), resulting in reduced rainfall—often less than 2 inches (5 cm) per month—and periodic droughts that concentrate water in sloughs and tree islands. These bimodal patterns arise from the interplay of subtropical high-pressure systems dominating winter and the northward migration of the Intertropical Convergence Zone in summer, creating a pulsed hydrologic regime essential to the ecosystem's marl prairie and sawgrass formations.[16][19][20] Extreme weather events, particularly hurricanes, punctuate these patterns, with the region vulnerable to Atlantic basin storms due to its coastal exposure; historical data record over 100 wind events, including major impacts from Hurricane Andrew (1992, Category 5), Wilma (2005), and Irma (2017, Category 4), which deliver intense rainfall exceeding 20 inches (51 cm) in hours, storm surges, and winds over 140 mph (225 km/h), reshaping vegetation through defoliation and sediment deposition. Such events, occurring roughly every 2–3 years on average in south Florida, temporarily alter salinity gradients and nutrient cycling but contribute to long-term mangrove losses totaling 547 km² from 1986 to 2022, as quantified by satellite analyses, though recovery varies by site hydrology. Droughts, conversely, intensify in El Niño years, reducing water levels by up to 50% and stressing wetland species, underscoring the Everglades' sensitivity to interannual variability in the subtropical climate regime.[21][22][23]

Ecosystems and Biodiversity

Sawgrass Marshes and Sloughs

Sawgrass marshes and sloughs constitute the ridge-and-slough mosaic that dominates the freshwater portions of the central and southern Everglades, forming an expansive, hydrologically connected system of parallel elevated ridges and deeper channels.[24] This landscape, characterized by low-nutrient conditions and prolonged inundation, historically covered about 55% of the pre-drainage Everglades area.[25] Sawgrass (Cladium jamaicense), a perennial sedge with sharp, serrated leaves, forms the primary vegetation on ridges, growing in dense stands up to 2.7 meters tall on peat substrates derived from accumulated organic matter.[26][27] Ridges typically measure 30 to 762 meters in width and extend 2 to 8 kilometers in length, elevated roughly 20 centimeters above adjacent sloughs, which promotes slightly drier conditions favoring sawgrass dominance over more aquatic species.[28][29] Sloughs, narrower at 91 to 396 meters wide, serve as primary conduits for slow-moving sheet flow, a process that historically maintained water clarity by allowing the slow trickling of low-phosphorus rainwater over the porous limestone bedrock, preventing stagnation and the proliferation of dense floating plants that would cloud the water, thereby sustaining vast sawgrass prairies with clear sloughs; these channels retain water depths that support floating plants like bladderworts (Utricularia spp.) and water lilies (Nymphaea odorata), with hydroperiods exceeding 11 months annually.[10][28][30] These channels remain flooded nearly year-round, even during dry seasons, facilitating nutrient transport and habitat connectivity.[31] Hydrologic regime drives the structural integrity of this ecosystem, with unidirectional southwesterly flow at velocities of 0.5 to 5 centimeters per second maintaining vegetation zonation through shear stress and water depth gradients.[32][9] Disruptions from drainage have led to sawgrass encroachment into sloughs, reducing open water and altering biodiversity by favoring ridge species in former channel habitats.[33] Key examples include Shark River Slough, a major flow path spanning Everglades National Park, which integrates marshes, tree islands, and ponds while supporting diverse aquatic communities.[34] Ecologically, these habitats sustain wading birds, fish, and invertebrates adapted to oligotrophic conditions, with peat accumulation rates historically balancing decomposition in the subtropical climate.[24] Restoration efforts prioritize reinstating natural hydroperiods to prevent further degradation, as shortened inundation promotes cattail invasion and peat loss.[35][9]

Hardwood Hammocks and Pinelands

Hardwood hammocks are dense, closed-canopy forests of broadleaf evergreen and semi-deciduous trees elevated on slight rises of limestone or organic buildup above surrounding wetlands, occurring sporadically throughout the Everglades from Shark River Slough to the eastern boundary. These tree islands form through gradual accumulation of leaf litter and peat on minor topographic highs, creating drier microhabitats amid the wet prairies and sloughs. Common canopy species include gumbo-limbo (Bursera simaruba), pigeon plum (Coccoloba diversifolia), and white stopper (Eugenia axillaris), with laurel oak (Quercus laurifolia) prominent in northern reaches; understories feature ferns, air plants, and shrubs like wild coffee (Psychotria nervosa).[36][37][38] In southern hammocks, tropical species dominate due to proximity to Caribbean flora, while northern variants incorporate temperate hardwoods like live oak (Quercus virginiana), reflecting a north-south gradient in tree composition driven by frost frequency and soil drainage. These habitats host high plant diversity, with over 100 tree and shrub species per hammock, and provide essential dry refuges for amphibians, reptiles, and mammals during floods, including the endangered Florida panther (Puma concolor coryi), which prefers mature hammocks for denning. Hammocks also trap seeds and organic matter, stabilizing islands against erosion in slow-moving sheetflow.[37][18] Pinelands, or pine rocklands, comprise open-canopy stands of South Florida slash pine (Pinus elliottii var. densa) rooted in thin soils over exposed oolitic limestone, primarily on Long Pine Key and Rocky Glades within Everglades National Park, covering about 10% of the park's upland area as of 1990s surveys. These ecosystems originate on karstic elevations where solution holes and thin marl allow pine establishment, with fires every 3–7 years clearing underbrush and promoting pine regeneration via serotinous cones and thick bark adaptations. Understories include saw palmetto (Serenoa repens), grasses like muhly (Muhlenbergia capillaris), and over 200 herbaceous species, many endemic and fire-dependent for germination.[39][40][41] Frequent lightning-ignited fires maintain pineland structure by suppressing hardwood invasion, as slash pines outcompete hardwoods post-fire due to rapid juvenile growth; fire exclusion since the mid-20th century has reduced pine densities from historical averages of 500–1,000 stems per hectare to under 200 in unburned stands. Pinelands support distinct fauna, including the Florida grasshopper sparrow (Ammodramus savannarum floridanus) and pine barren treefrog (Hyla andersonii), and act as corridors connecting hammocks for dispersal. Both hammocks and pinelands, as the Everglades' primary uplands, contrast with wetland dominance by offering aerobic soils and elevation differences of 1–3 meters, fostering biodiversity hotspots vulnerable to altered hydrology and invasive species like Brazilian pepper (Schinus terebinthifolia).[42][43][39]

Cypress Swamps and Mangroves

Cypress swamps in the Everglades consist of forested wetlands dominated by bald cypress (Taxodium distichum) and pond cypress (Taxodium ascendens), which thrive in persistently flooded, low-nutrient conditions with standing water depths often exceeding several feet during wet seasons.[44][45] These deciduous conifers produce characteristic "knees"—pneumatophores protruding above the water surface to facilitate gas exchange in oxygen-poor soils—and buttressed trunks for stability in soft substrates.[46] Bald cypress predominates in deeper sloughs like Shark River Slough, while pond cypress occurs in shallower, nutrient-impoverished areas; both species shed needles annually, contributing organic matter that supports detritus-based food webs.[18][47] These swamps, covering significant portions of Big Cypress Swamp—over 700,000 acres of freshwater habitat—act as hydrologic buffers, slowing sheet flow and filtering nutrients before water reaches downstream marshes.[48] Hydrologically, cypress swamps depend on consistent freshwater inundation from seasonal rainfall and upstream runoff, with hydroperiods historically spanning 6–9 months annually; reductions in water depth due to drainage have stressed old-growth stands, as evidenced by decreased hydroperiods of 18% in some areas from the 1960s to 2010s despite stable rainfall.[49][50] Fauna includes wading birds like wood storks nesting in canopies, alligators using root systems for thermoregulation, and fish such as gar in flooded understories, while understory plants like ferns and air plants tolerate shade and periodic drying.[44] These ecosystems span from central Big Cypress National Preserve northward into adjacent watersheds, forming a transition between prairies and coastal zones.[45] Mangrove forests fringe the southern Everglades coast, occupying over 550 square miles—the largest such expanse in the continental United States—and transition freshwater outflows into saline environments along channels, rivers, and Florida Bay.[51] Three primary species structure these zonated communities: red mangroves (Rhizophora mangle) pioneer seaward edges with prop roots arching into intertidal zones; black mangroves (Avicennia germinans) occupy slightly higher, less saline interiors with pneumatophores for aeration; and white mangroves (Laguncularia racemosa) inhabit upland fringes, least tolerant to cold but intermixed with the others.[52][53] These halophytic trees exclude salt via root membranes and excrete excess via leaves, enabling survival in salinities up to 90 parts per thousand.[54] Ecologically, mangroves serve as nurseries for over 220 fish species, including snappers and tarpon, by trapping sediments and organic detritus in root mats that foster invertebrate prey; they also stabilize shorelines, attenuating wave energy and reducing erosion during storms, with wider forests providing greater flood mitigation.[55][56] Bird diversity includes 181 species using habitats for foraging, such as roseate spoonbills in prop-root perches, while mammals like manatees graze associated seagrasses.[57] As carbon sinks, these forests rank among the most productive coastal ecosystems, sequestering nutrients and buffering upstream freshwater systems from tidal surges, though sea-level rise has prompted inland migration in some areas since the 1980s.[58][5] Distribution extends from Everglades National Park's southern boundaries northward along the Gulf and Atlantic coasts, with black mangroves extending farthest inland due to greater salinity tolerance.[59]

Key Flora, Fauna, and Biodiversity Hotspots

The Everglades ecosystem harbors exceptional biodiversity, with approximately 1,033 plant taxa, 76 mammal species, over 400 bird species, 60 reptile taxa, and 300 fish species documented in Everglades National Park.[60] Among the 36 threatened or endangered species, key fauna include the Florida panther (Puma concolor coryi), with fewer than 100 individuals remaining, the American crocodile (Crocodylus acutus), West Indian manatee (Trichechus manatus), snail kite (Rostrhamus sociabilis), and wood stork (Mycteria americana).[61][62] The American alligator (Alligator mississippiensis) functions as a keystone species, creating "gator holes" that retain water and sustain aquatic life during dry periods.[18] Dominant flora encompass sawgrass (Cladium jamaicense), forming the largest continuous stand of sawgrass prairie in the world, bald cypress (Taxodium distichum) in swamps, and mangrove species—red (Rhizophora mangle), black (Avicennia germinans), and white (Laguncularia racemosa)—comprising the Western Hemisphere's largest mangrove ecosystem.[63] Epiphytic orchids number 39 native species, alongside bromeliads and wildflowers that add to the region's floral diversity.[64] Rare plants in hardwood hammocks and pinelands include the brittle thatch palm (Thrinax morrisii) and buccaneer palm (Pseudophoenix sargentii), both threatened by habitat loss and sea-level rise.[65] Biodiversity hotspots within the Everglades concentrate endemic and endangered species, notably tree islands, which act as nutrient-rich refugia supporting elevated plant and animal densities amid surrounding wetlands.[66] Sloughs such as Shark River Slough channel sheet flow and foster high concentrations of wading birds and aquatic organisms, while coastal mangrove fringes and Florida Bay serve as nurseries for marine fish and invertebrates, hosting breeding grounds for species like the roseate spoonbill (Platalea ajaja).[67][68] These areas underscore the Everglades' role as a global biodiversity hotspot, with unique assemblages not replicated elsewhere.[69]

Human History and Modification

Indigenous Inhabitants and Early Use

The Calusa people, who inhabited the southwest Florida region including parts of the Everglades from approximately 100 CE until the mid-1700s, formed a hierarchical society estimated to number 20,000 to 50,000 individuals, subsisting primarily through fishing, hunting, and gathering without reliance on agriculture.[70] They constructed extensive shell mounds and middens from oyster and other shellfish remains, which served as platforms for villages and ceremonial structures, with archaeological sites revealing keyhole-shaped houses and canal systems for canoe navigation.[71] These adaptations exploited the wetland's aquatic resources, including fish traps and nets documented in ethnohistoric accounts from Spanish explorers.[72] In the southeast Everglades and adjacent Biscayne Bay areas, the Tequesta tribe maintained smaller, decentralized communities focused on coastal and estuarine foraging, with evidence of shell tool manufacturing and burial mounds dating to around 500 BCE.[73] Archaeological surveys across hundreds of tree island sites indicate widespread prehistoric human modification of the landscape, such as clearing for habitation and resource extraction, predating the full Holocene formation of the modern Everglades by millennia.[74][75] These groups' practices, including seasonal migrations via dugout canoes, sustained populations amid the region's seasonal flooding and resource variability.[72] European contact in the 16th century, via Spanish expeditions, introduced diseases that decimated Calusa and Tequesta populations, leading to their near-extinction by the early 18th century.[72] By the late 18th century, Seminole and Miccosukee peoples, migrating southward from Creek confederacies in Georgia and Alabama around 1715–1783, began utilizing the Everglades as a refuge and foraging ground, building chickee huts on raised platforms and hunting alligators, deer, and fish while incorporating limited maize cultivation on higher grounds.[76][77] These groups' oral histories and archaeological traces link partial ancestry to pre-contact Florida indigenous populations, though their adaptation emphasized mobility and wetland exploitation during conflicts like the Seminole Wars (1816–1858).[78]

European Exploration and Initial Settlement

European exploration of the Everglades began with Spanish expeditions in the early 16th century. Juan Ponce de León landed on Florida's east coast in 1513, sailing southward to Florida Bay and the Ten Thousand Islands, claiming the region for Spain but encountering resistance from indigenous Calusa groups.[79] In 1521, Ponce de León returned with about 200 colonists to establish a settlement near Charlotte Harbor, but the effort failed after Calusa warriors repelled the intruders, wounding Ponce de León mortally.[79] Spanish cartographers subsequently depicted the Everglades on maps as a vast, unmapped wetland, though few ventured inland due to the terrain and hostile inhabitants.[80] During the Spanish colonial period, interactions remained coastal and limited. Pedro Menéndez de Avilés founded St. Augustine in 1565 and negotiated with Calusa and Tequesta leaders in 1566 to secure missions, but these efforts did not penetrate the interior marshes.[79] From the 1730s to 1821, Spanish fishermen operated up to 12 smacks annually from Charlotte Harbor to Cape Sable, establishing temporary camps in Florida Bay and the Ten Thousand Islands to harvest mullet, kingfish, and mackerel for Havana markets.[79] British control from 1763 to 1784 introduced surveys by Bernard Romans, who in 1771 documented Calusa sites at Cape Sable and published observations on regional flora and fauna in 1775.[79] Spain regained Florida in 1784, with Andrew Ellicott surveying Cape Sable in 1789.[79] After the U.S. acquired Florida in 1821, exploration intensified amid the Seminole Wars, prompting military expeditions into the wetlands. During the Second Seminole War (1835–1842), the U.S. Army established Fort Poinsett in 1838 near the Shark River, evacuating it by May due to disease and logistics, with brief reoccupation in 1839–1840.[79] In 1857, Fort Cross was built on the Harney River in January and abandoned by June, while Camp Moulder operated briefly on Chokoloskee Island and Pavilion Key.[79] Scientific efforts included John James Audubon's 1832 traversal of Florida Bay, Key West, Cape Sable, and Sandy Key to collect bird specimens.[79] Buckingham Smith's 1847 expedition assessed drainage potential, reporting to Congress in 1848 that canals could reclaim land at a cost of up to $500,000, though no immediate action followed.[79] Initial European settlement occurred on the periphery in the mid-19th century, constrained by flooding, insects, and Seminole presence. Dr. Henry Perrine attempted tropical plant cultivation near Cape Sable in 1838 under a land grant but was killed during the Seminole War in 1840.[79] During the Civil War, John Weeks grew vegetables at Cape Sable from 1861 to 1865 to supply Union forces at Key West.[79] Permanent outposts emerged in the late 1860s, with Weeks and Adolphus Santini settling Chokoloskee Island for fishing and hunting; by the 1870s, homesteaders occupied sites along the Lostmans and Turner Rivers in the Ten Thousand Islands.[79] These early communities relied on subsistence farming, hunting, and trade, avoiding the deeper marshes until drainage schemes in the 1880s.[81]

19th-Century Drainage Efforts

The first major organized attempts to drain the Everglades for agricultural and settlement purposes began in the late 19th century, amid a national push for land reclamation and expansion. Proposals to convert the wetlands into plantations date back to 1848, but practical efforts did not commence until 1881, when Philadelphia industrialist Hamilton Disston negotiated a contract with Florida's Internal Improvement Fund trustees.[82][83] On March 10, 1881, Disston's Atlantic and Gulf Coast Canal and Okeechobee Land Company agreed to drain approximately 4 million acres of swamp and overflowed lands south of Lake Okeechobee, paying $1 million upfront in exchange for ownership of half the reclaimed acreage. Work started on November 7, 1881, focusing on canal construction to redirect water flow. Key projects included the Cross Prairie Canal, Southport Canal (completed in 1883), connections between Lakes Cypress, Hatchineha, and Kissimmee, and a critical link from Lake Okeechobee to Lake Hicpochee, which provided the first tidal outlet for Okeechobee via the Caloosahatchee River.[83][84] These initiatives lowered Lake Okeechobee's water level by about 4.5 feet and enabled reclamation of over 1.1 million acres by 1893, facilitating town foundations like Kissimmee and St. Cloud, as well as agricultural ventures such as the St. Cloud Sugar Plantation established in 1887. However, progress was hampered by disputes over land claims, exaggerated reclamation reports leading to a 1885 investigation, and the inherent challenges of the Everglades' porous limestone bedrock and slow sheet flow, which resisted full drainage. Financial strains from the Panic of 1893 further limited success, and by Disston's death in 1896, much of the region remained wetland, though his work demonstrated partial feasibility and spurred ongoing interest.[83][84]

20th-Century Urban Expansion and Agriculture

Expanded dredging efforts from 1905 to 1910 converted large wetland tracts into agricultural and developable land south of Lake Okeechobee, fueling population influx and settlement in the region.[85] This infrastructure supported rapid urbanization, particularly in Miami, where the city's population surged from approximately 5,500 residents in 1910 to nearly 30,000 by 1920, driven by real estate speculation during the Florida land boom.[86] By 1950, Miami's population reached 249,276, reflecting sustained post-World War II migration and economic expansion that encroached on former Everglades margins.[87] Agricultural development paralleled urban growth, with drained lands initially used for vegetable farming and muck soil cultivation near Belle Glade.[3] In the 1920s, the state established the Everglades Experiment Station in Belle Glade, and the U.S. Department of Agriculture founded a sugarcane field laboratory, promoting crop experimentation suited to the peat soils.[3] Sugarcane cultivation gained prominence after initial vegetable trials, bolstered by federal protections during the Great Depression, leading to the construction of major mills by 1930 and industry consolidation under entities like U.S. Sugar Corporation, which by 1940 dominated production in the area.[88] The 1948 Central and Southern Florida Flood Control Project formalized the Everglades Agricultural Area (EAA), designating over 470,000 acres south of Lake Okeechobee for intensive farming, primarily sugarcane, which became the dominant crop due to its profitability on the reclaimed organic soils.[89] This zone, now encompassing around 700,000 acres with most under cultivation, generated significant revenue—exceeding $700 million annually from sugarcane by the late 20th century—while urban pressures from expanding metropolises like Miami further fragmented the hydrological connectivity of the original Everglades system.[90] Between 1900 and the late 20th century, approximately 11,027 square kilometers of natural South Florida landscapes shifted to agricultural and urban uses, with urban land cover expanding markedly to accommodate population booms.[91]

Flood Control and Infrastructure

Central and Southern Florida Project

The Central and Southern Florida (C&SF) Project, authorized by Congress through the Flood Control Act of 1948, constitutes a vast multi-purpose water management system engineered to mitigate flooding, supply water, prevent saltwater intrusion, and facilitate navigation across central and southern Florida.[92] [93] The U.S. Army Corps of Engineers designed the project, which the South Florida Water Management District operates and maintains, encompassing approximately 16 million acres and delivering flood protection alongside water for over 6 million residents and nearly 1 million acres of agricultural land.[94] [92] Core infrastructure includes over 1,000 miles of canals and levees, more than 150 water control structures, and 16 major pump stations, which channel and regulate water flows from Lake Okeechobee southward and eastward to coastal outlets.[95] [93] Construction commenced in the early 1950s following devastating 1947 floods that prompted the authorization, with major features substantially completed by 1973.[95] [96] Prominent elements encompass the reinforced Hoover Dike encircling Lake Okeechobee to avert overflows, eastern perimeter levees blocking natural eastward seepage, and compartmentalized Water Conservation Areas (WCAs) that impound water for controlled release.[92] [95] By redirecting sheet flows into linear canals, the project effectively curtailed basin-wide inundation risks—such as those from hurricanes—but substantially altered pre-existing hydrology, reducing southward delivery to Everglades National Park by about 40% of historic volumes and fragmenting wetlands into isolated compartments.[93] [95] Subsequent amendments under Flood Control Acts of 1954, 1962, and others expanded scopes for ecosystem preservation, though initial implementation prioritized development by enabling drainage for agriculture and urban expansion.[97] [98]

Everglades Agricultural Area

The Everglades Agricultural Area (EAA), located immediately south of Lake Okeechobee in southern Florida, comprises approximately 700,000 acres designated primarily for intensive crop production following extensive drainage and flood control measures.[99] This region, which accounts for about 27 percent of the Kissimmee-Okeechobee-Everglades watershed, was formally established under the Central and Southern Florida (C&SF) Project authorized by Congress in 1948, initially encompassing over 480,000 acres to support agricultural development on former wetland soils.[100] Water management infrastructure, including canals and levees, was largely completed by 1962, enabling the conversion of organic-rich peat soils into farmland suitable for row crops. Sugarcane dominates EAA agriculture, occupying roughly 400,000 acres and generating annual economic output exceeding $1 billion through exports and domestic sales, with farms managed by large-scale operations under strict seasonal flooding and draining cycles to optimize yields on subsidence-prone soils.[101] Other crops include rice, vegetables, and sod, but sugarcane's high nutrient demands—particularly phosphorus fertilizers—have led to significant runoff into downstream ecosystems, historically elevating phosphorus concentrations in discharges to levels 40 times above natural baselines in the northern Everglades.[102] In response, the 1994 Everglades Forever Act mandated best management practices (BMPs) across EAA farms, targeting a 25 percent reduction in phosphorus loads through measures like precision fertilization and tailwater recovery systems, which peer-reviewed analyses confirm achieved average annual outflows below 40 parts per billion by the early 2000s.[103][104] To meet stricter standards of 10 parts per billion phosphorus for Everglades protection, four stormwater treatment areas (STAs) totaling over 40,000 acres were constructed downstream of the EAA between 1994 and 2011 at a cost of approximately $2 billion, utilizing constructed wetlands to filter agricultural effluents via vegetative uptake and sedimentation before release southward.[102] Despite these advancements, restoration under the Comprehensive Everglades Restoration Plan (CERP) faces challenges in the EAA, including debates over land acquisition for additional reservoirs—proposals to purchase up to 150,000 acres of farmland have met resistance due to economic dependencies—while ongoing subsidence from soil oxidation continues to lower elevations, complicating sheet flow restoration to Florida Bay.[105] Federal and state monitoring data indicate that while BMPs and STAs have curbed point-source pollution, diffuse nutrient legacies persist, underscoring the causal link between decades of high-input monoculture and altered hydrologic regimes.[3]

Canals, Levees, and Reservoirs

The Central and Southern Florida (C&SF) Project, authorized by the U.S. Congress in 1948, established a vast infrastructure of canals and levees to control flooding, provide water supply, and support agriculture and urban development across south Florida, including the Everglades watershed.[106] This system encompasses roughly 1,000 miles (1,600 km) of canals and an equivalent length of levees, complemented by 150 water control structures and 16 major pump stations that regulate flows from Lake Okeechobee southward.[96] These features fundamentally altered the natural sheetflow of the Everglades by channeling water into linear paths, reducing overland flow and compartmentalizing the landscape into managed basins such as the Water Conservation Areas (WCAs).[107] Key canals include the C-4 Tamiami Canal, a 50-mile (80 km) waterway paralleling U.S. Highway 41 and serving as the northern boundary for much of Everglades National Park, constructed in the 1920s and expanded under the C&SF Project to divert water eastward.[108] The Miami Canal (C-6), extending 28 miles (45 km) from Lake Okeechobee to Miami, facilitates drainage for the Everglades Agricultural Area (EAA) and urban supply.[109] Additional major canals, such as the C-38 (Hillsboro Canal) and C-51 (West Palm Beach Canal), connect the lake to coastal outlets, with early 20th-century precursors like the four primary channels dug by 1917 from the lake to the Atlantic Ocean forming the backbone of initial drainage efforts.[110] The South Florida Water Management District oversees nine principal regional canals, including C-1 (Black Creek), C-2 (Snapper Creek), and C-9 (Snake Creek), which border urbanized coastal ridges and intercept rainfall runoff.[111] Levees form critical barriers in the system, with the 100-mile (160 km) eastern perimeter levee—a 10- to 20-foot (3- to 6-meter) high earthen berm—shielding agricultural and developed lands east of the Everglades from overflows.[112] The L-67 complex encircles the WCAs, impounding freshwater to prevent seepage into adjacent areas while controlling releases via structures like the S-8 and S-12 gates on Levee 29, which regulate entry into Everglades National Park.[106] The Hoover Dike, encircling Lake Okeechobee since the 1920s and reinforced post-1947 hurricane, exemplifies early flood defenses, spanning 143 miles (230 km) and standing up to 30 feet (9 m) high in sections to contain the lake's waters.[1] Reservoirs, initially limited but expanded for restoration, store excess water to mitigate discharges and restore natural hydroperiods. The Everglades Agricultural Area Reservoir, a 10,500-acre (4,300 ha) facility with 240,000 acre-feet (300 million m³) capacity, captures Lake Okeechobee overflow for treatment in an adjacent 6,500-acre (2,600 ha) stormwater wetland before southward conveyance, with construction advancing under the Central Everglades Planning Project (CEPP) authorized in 2016.[113] Upstream, the C-43 Reservoir near the Caloosahatchee River, completed in July 2025, holds 55 billion gallons (208 million m³) across 10,000 acres (4,000 ha) at depths of 15-25 feet (4.5-7.6 m), reducing estuarine pollution from high-volume releases.[114] The C-44 Reservoir, finished earlier, similarly stores 43 billion gallons (163 million m³) for the St. Lucie River basin, integrating with C&SF infrastructure to balance flood control and ecological needs.[115]

Outcomes and Unintended Consequences

The Central and Southern Florida Project, implemented starting in 1948, achieved its primary goal of reducing catastrophic flooding across central and southern Florida, protecting urban areas, agriculture, and over six million residents while supplying water to nearly one million acres of farmland.[94] However, the project's 1,600-mile network of canals, levees, and control structures disrupted the Everglades' natural slow sheet flow, diverting approximately 1.7 billion gallons of water daily away from the ecosystem toward the coast or ocean.[116] A major unintended consequence has been the loss of more than 50% of South Florida's original wetlands since canal construction began in the early 20th century, as drainage enabled conversion to agriculture and development, fragmenting habitats and reducing overall wetland acreage from about nine million to fewer than four million acres.[107] Lowered water tables in the remaining Everglades, often dropping to depths that expose peat soils to air, have accelerated organic matter decomposition, leading to subsidence rates averaging 1.25 inches per year in drained areas since observations began in 1914.[117] This subsidence, driven by oxidation rather than cultivation alone, has lowered land elevations by several feet in places like the Everglades Agricultural Area, increasing vulnerability to flooding and complicating water management.[3] Reduced freshwater delivery has promoted saltwater intrusion into coastal marshes, mangrove fringes, and the Biscayne aquifer, where drainage since the early 1900s has pushed saline water inland, contaminating groundwater that supplies drinking water to millions and altering soil properties in wetlands.[118] In the Everglades Agricultural Area, canal discharges carrying agricultural runoff have elevated total phosphorus concentrations downstream from natural levels of 4-10 parts per billion (ppb) to as high as 100 ppb or more in affected areas by the 1980s, fostering invasive cattail expansion and eutrophication that degraded native sawgrass marshes.[119] Although best management practices implemented since the 1990s have reduced phosphorus loads by up to 70% in some monitoring periods, persistent high levels in certain hotspots continue to impair ecosystem recovery.[120] Hydrologic alterations have also reversed natural flow patterns, concentrated water in channels during wet seasons to exacerbate downstream flooding in some areas, and promoted abnormal fire regimes by drying out peat during prolonged low-water periods, further contributing to habitat loss and biodiversity declines in wading bird populations and other species dependent on consistent hydroperiods.[121] These changes underscore how flood control measures, while averting immediate human risks, have induced long-term ecological degradation requiring ongoing restoration interventions.[98]

Conservation and Restoration

National Park Establishment and Protection

Efforts to establish a national park in the Everglades began in 1928 when landscape architect Ernest F. Coe founded the Everglades Tropical National Park Association to advocate for preservation amid growing drainage and development pressures. Coe's campaign highlighted the unique subtropical wilderness, garnering support from scientists and conservationists concerned about ecosystem degradation from agricultural expansion. This advocacy culminated in congressional authorization of Everglades National Park on May 30, 1934, under Public Act No. 389, aiming to protect approximately 2 million acres of wetlands, forests, and coastal areas.[122] Land acquisition proved challenging due to private holdings and economic constraints during the Great Depression and World War II, delaying full establishment until December 6, 1947, when President Harry S. Truman dedicated the park in a ceremony at Everglades City.[123] At dedication, the park encompassed about 1.5 million acres, with the National Park Service assuming management responsibilities to conserve native flora and fauna, including rare species like the Florida panther and American crocodile.[123] Initial protections focused on prohibiting commercial exploitation and regulating public access to maintain ecological integrity, as mandated by the National Park Service Organic Act of 1916.[124] Subsequent legislation expanded protections, notably the Everglades National Park Protection and Expansion Act of 1989, signed by President George H.W. Bush on December 13, 1989, which authorized the acquisition of up to 346,000 additional acres, including the vulnerable "East Everglades" buffer zone threatened by urban sprawl from Miami.[125][126] This act addressed hydrological alterations from upstream canals that had reduced freshwater flows, emphasizing the need for integrated watershed management to sustain the park's biodiversity.[125] In 1979, the park was designated a UNESCO World Heritage Site and International Biosphere Reserve, underscoring its global ecological significance and committing the U.S. to stringent conservation standards.[124] These measures have preserved core habitats despite ongoing external pressures from water diversion and pollution.

Comprehensive Everglades Restoration Plan (CERP)

The Comprehensive Everglades Restoration Plan (CERP), authorized by the U.S. Congress through the Water Resources Development Act of 2000, establishes a collaborative framework between the federal government and the State of Florida to restore the natural hydrological regime of the Everglades while accommodating urban and agricultural water demands.[127][128] The plan addresses decades of ecosystem degradation caused by flood control infrastructure, aiming to recapture and redistribute lost freshwater flows—originally estimated at over 2 billion gallons per day diverted to the ocean or coastal areas—across approximately 2.4 million acres of wetlands, including Everglades National Park.[129] Core objectives include restoring the quantity, quality, timing, and spatial distribution of water to mimic pre-drainage conditions, thereby enhancing habitat for native species and reducing harmful discharges to estuaries like Florida Bay and the Caloosahatchee River.[130][131] CERP encompasses 68 distinct project components, implemented primarily by the U.S. Army Corps of Engineers (USACE) and the South Florida Water Management District (SFWMD) under a 50-50 federal-state cost-sharing arrangement, with total estimated costs exceeding $23 billion as of initial projections, though actual expenditures have risen due to delays and scope adjustments.[132][99] Key elements include constructing reservoirs for water storage (e.g., the Central Everglades Planning Project, or CEPP, designed to store and treat up to 370,000 acre-feet annually from Lake Okeechobee), seepage barriers to prevent underground losses, stormwater treatment areas for phosphorus reduction, and canal modifications to facilitate southward flows.[133][115] These components prioritize adaptive management, incorporating scientific modeling to adjust designs based on empirical monitoring of hydrology, water quality, and ecological responses.[134] Implementation has proceeded incrementally since 2000, with biennial progress reports to Congress documenting advancements such as the completion of 60+ project features by 2020 and ongoing constructions like the C-43 stormwater treatment area reservoir, operational as of June 1, 2025, which captures agricultural runoff to improve Caloosahatchee River water quality.[135][136][114] Florida's 2025-2026 budget allocates $1.4 billion toward CERP and related initiatives, supporting groundbreakings and water deliveries that have increased southward flows by millions of gallons daily in recent years.[137][138] However, challenges persist, including chronic funding shortfalls—federal appropriations have lagged behind state investments—legal disputes over land acquisition and environmental impacts, and opposition from agricultural stakeholders concerned about water supply reliability.[128][139] Independent reviews, such as those from the National Academies, highlight difficulties in achieving water quality targets due to persistent phosphorus loading and the complexity of restoring sheetflow dynamics amid urban encroachment, with full system-level benefits projected beyond 2030 despite partial successes in habitat recovery.[140][141]

Water Quality and Invasive Species Management

Water quality in the Everglades has been degraded primarily by phosphorus runoff from agricultural activities in the Everglades Agricultural Area (EAA), leading to eutrophication, algal blooms, and shifts in native vegetation toward cattail-dominated marshes since the 1960s.[102] To address this, the South Florida Water Management District (SFWMD) constructed Stormwater Treatment Areas (STAs), large artificial wetlands that filter phosphorus through vegetative uptake, sedimentation, and microbial processes, achieving long-term load reductions of up to 80-90% in some facilities.[142] [143] These STAs, operational since the 1990s, target a phosphorus criterion of 10 micrograms per liter for discharges into the Everglades Protection Area, with monitoring showing improved trends in total phosphorus concentrations in Water Conservation Areas post-implementation.[144] [145] Mercury contamination poses another persistent challenge, stemming from atmospheric deposition that undergoes microbial methylation in the anaerobic conditions of Everglades wetlands, resulting in elevated methylmercury levels in fish exceeding consumption advisory thresholds in over 60% of sampled areas.[146] [147] Agricultural sulfur inputs exacerbate methylation rates, amplifying bioaccumulation in the food web, while management strategies include reducing sulfur applications, restoring natural hydrology to limit deep-water pooling, and controlling marsh fires to minimize organic matter that fuels methylation.[147] [148] The Comprehensive Everglades Restoration Plan (CERP), authorized in 2000, integrates water quality enhancements by expanding treatment infrastructure and monitoring via programs like the EPA's Regional Environmental Monitoring and Assessment Program (REMAP).[129] [149] Invasive species management targets both flora and fauna that disrupt native ecosystems, with Burmese pythons—introduced via the pet trade—responsible for population declines of up to 90% in small- and medium-sized mammals since their establishment around 2000, prompting annual removal efforts yielding over 10,000 individuals by 2021 through hunts, detector dogs, and interagency collaborations.[150] [151] Plant invaders like melaleuca trees, which alter fire regimes and hydrology by forming dense stands that reduce open marsh, are controlled using herbicides, prescribed flooding, and biological agents such as the melaleuca psyllid, with SFWMD treating millions of acres to support restoration.[152] Other species, including Brazilian peppertree and Old World climbing fern, receive similar integrated pest management, though challenges persist due to rapid spread and seed dispersal.[153] CERP indirectly aids by restoring sheetflow to disadvantage invasives favoring altered conditions, while the National Park Service employs strategic eradication in priority habitats.[154] [129] Despite progress, invasive species continue to hinder full ecosystem recovery, necessitating ongoing research into detection and suppression technologies.[155]

State-Led Initiatives and Progress

The state of Florida, through agencies like the South Florida Water Management District (SFWMD) and the Department of Environmental Protection, has prioritized Everglades restoration with unprecedented funding and project acceleration since 2019. Under Governor Ron DeSantis, investments have exceeded $8 billion, including $1.4 billion in the Fiscal Year 2025-26 budget, surpassing prior administrations' commitments and enabling over 75 projects to be completed or launched.[115][156] These efforts focus on enhancing water storage, treatment, and southward flows to mitigate historical drainage impacts and support ecosystem recovery. Key state-led advancements include the completion of the C-43 and C-44 stormwater treatment reservoirs, which capture and clean excess water from the St. Lucie and Caloosahatchee watersheds before release to estuaries, reducing harmful discharges.[115] The groundbreaking for the Blue Shanty Flow Way in 2025, under a new state-federal agreement, aims to restore sheetflow to Everglades National Park and Florida Bay, with completion accelerated by two years.[115] State funding has tripled water storage capacity to 176 billion gallons across reservoirs and treatment areas, facilitating the Central Everglades Planning Project's delivery of 370,000 acre-feet of water annually to degraded habitats.[115] Measurable progress includes significant nutrient load reductions—1.8 million pounds of nitrogen and 770,000 pounds of phosphorus annually—achieved via expanded stormwater treatment areas (STAs) that filter agricultural runoff before it reaches the Everglades Agricultural Area.[115] The SFWMD's 2025 South Florida Environmental Report documents record hydrologic conditions, improved phosphorus levels in monitoring wells, and increased clean water volumes directed southward, with ongoing construction on the EAA Reservoir projected for operational status by 2029 to further isolate polluted discharges.[138] These outcomes reflect state-driven momentum in reversing phosphorus enrichment and hydrologic alterations, though long-term ecological responses require continued monitoring.[138]

Economic and Societal Impacts

Tourism and Recreational Value

The Everglades attract approximately 750,000 to 1 million visitors annually to Everglades National Park, with 810,189 recorded in 2023 and 741,983 in 2024, supporting ecotourism focused on the region's unique subtropical wetland ecosystem.[157][158] Tourism generates significant economic activity, including $58.7 million in visitor spending at Everglades National Park alone in recent years, contributing to broader South Florida national park tourism benefits of $225 million annually.[159] This spending sustains 803 jobs directly tied to the park, alongside thousands more in related sectors like hospitality and guiding services.[159] Popular recreational activities include wildlife viewing along trails such as the Anhinga Trail and Shark Valley loop, where visitors observe alligators, birds, and manatees; guided airboat tours in adjacent areas; kayaking and canoeing through mangrove tunnels; and fishing in Florida Bay.[160][161] Biking the 15-mile Shark Valley tram road and ranger-led hikes provide low-impact access to sawgrass prairies and hardwood hammocks, emphasizing the Everglades' role as a biodiversity hotspot with over 350 bird species and endangered species like the Florida panther.[161] These pursuits not only offer immersive experiences in a rare "River of Grass" landscape but also educate on conservation, though high visitation strains resources and requires sustainable management to prevent overcrowding.[17] The recreational value extends to hunting, camping, and boating in Big Cypress National Preserve and state areas, bolstering Florida's $100 billion tourism industry, where Everglades-related activities draw international visitors seeking authentic wilderness encounters.[162] Economic analyses estimate the Everglades ecosystem, including tourism, contributes $31.5 billion yearly to South Florida's economy through visitor expenditures on lodging, tours, and equipment rentals.[163] Restoration efforts, such as those under the Comprehensive Everglades Restoration Plan, aim to enhance these values by improving water flows and habitats, potentially increasing long-term recreational opportunities amid challenges like invasive species and sea-level rise.[164]

Agricultural Productivity and Water Supply

The Everglades Agricultural Area (EAA), spanning about 700,000 acres immediately south of Lake Okeechobee, has been transformed from wetlands into fertile farmland since the early 20th century through extensive drainage and canal construction.[85] This region produces over half of the United States' sugarcane, with Florida's output reaching 18 million tons in 2024, predominantly from the EAA's 410,000 acres dedicated to the crop.[165][166][167] Sugarcane cultivation in the EAA generates more than $2 billion annually in direct and indirect economic value, supporting jobs in farming, processing, and transportation across counties like Palm Beach, Hendry, Glades, and Martin.[168] Agricultural productivity in the EAA relies on the rich, organic muck soils derived from decomposed peat after drainage, enabling high yields of sugarcane, rice, and sod, though long-term subsidence from oxidation poses sustainability challenges.[165] Farmers in the area have invested over $450 million since the 1990s in water treatment infrastructure and best management practices to manage runoff while maintaining output.[169] The broader Everglades ecosystem underpins South Florida's water supply by naturally filtering and recharging the Biscayne Aquifer, which delivers freshwater to nearly 8 million people for drinking, bathing, and urban uses—accounting for more than half of regional consumption—plus irrigation for agriculture.[170][171] One-third of Florida's population depends on this aquifer replenishment from Everglades sheetflow, historically disrupted by diversions for flood control and farming.[68] Water management in the EAA involves pumping from Lake Okeechobee via canals for irrigation, which sustains crop productivity but competes with urban demands and restoration goals to redirect flows southward for aquifer recharge and ecosystem health.[1] Conflicts arise as increased storage reservoirs proposed under restoration plans could limit available water for agriculture or require land buyouts, potentially affecting yields in this high-value area.[172] Despite these tensions, EAA farming contributes to regional water security by utilizing excess lake water that might otherwise cause flooding.[171]

Broader Economic Contributions and Cost-Benefit Analysis

The Everglades ecosystem provides flood protection valued at approximately $4.5 billion annually by mitigating storm surges and reducing inland flooding risks for South Florida's urban areas, a service enhanced by intact wetlands that absorb and slow water flows during hurricanes.[164] Mangrove forests within the system store carbon equivalent to $2 billion to $3.4 billion based on sequestration rates measured in 2016, contributing to global climate regulation through long-term burial of organic matter in anoxic soils.[173] Commercial and recreational fisheries supported by Everglades nutrient cycling and habitat generate indirect economic value exceeding $100 million yearly in landings, with restoration projected to add $2.04 billion in net present value for angling alone.[174] These services underpin broader regional prosperity, including $9.2 billion in annual real estate value enhancement from preserved natural buffers that stabilize property markets against sea-level rise and erosion.[175] A 2025 analysis estimates the system's total annual economic output at $31.5 billion, encompassing water filtration that averts treatment costs for municipal supplies and biodiversity maintenance supporting ecotourism multipliers.[163] Over 50 years, undiminished ecosystem functions could yield $1 trillion in cumulative natural capital benefits, far outpacing direct sectoral inputs like agriculture.[176] Cost-benefit evaluations of restoration under the Comprehensive Everglades Restoration Plan (CERP), initiated in 2000, indicate benefit-cost ratios ranging from 4:1 overall to 8.1:1 for specific components like the proposed South Reservoir, where $20 billion in projected flood mitigation and habitat gains offset infrastructure expenses.[177][178] Net present value analyses project $46.5 billion in total economic gains from enhanced services, potentially reaching $123.9 billion under optimistic hydrologic recovery scenarios, against CERP's updated $23.2 billion total cost as of 2020.[179][180] Annual ecosystem service uplifts from targeted hydrologic restoration are estimated at $1.18 billion to $1.53 billion, driven by improved freshwater delivery that causal modeling links to biodiversity rebounds and reduced salinity intrusion.[181] These ratios hold despite implementation delays, as empirical data from partial projects affirm causal links between restored sheetflow and service delivery, though full realization depends on adaptive management amid invasive species pressures.[182]

Controversies and Future Challenges

Debates Over Development vs. Preservation

Efforts to develop the Everglades began in the late 19th century with drainage projects led by figures like Hamilton Disston, who in 1881 secured state contracts to reclaim land for agriculture by constructing canals, though many failed due to the region's porous limestone substrate.[3] By the early 20th century, state and federal initiatives accelerated draining, converting over half of the original Everglades wetland into agricultural and urban areas, primarily for sugarcane farming in the Everglades Agricultural Area (EAA) and expansion of cities like Miami.[141] These developments provided economic benefits, with sugarcane production alone contributing approximately $4.68 billion annually to Florida's economy through farming, processing, and related jobs.[183] The establishment of Everglades National Park in 1947 marked a shift toward preservation, driven by ecological concerns over habitat loss and species decline, yet development pressures persisted, particularly after the 1947 hurricanes prompted the U.S. Army Corps of Engineers' Central and Southern Florida (C&SF) Project in 1948, which built levees, canals, and reservoirs for flood control, water supply to agriculture and urban areas, and further land reclamation.[127] This project reduced natural sheetflow through the Everglades by about 70%, leading to ecosystem degradation including peat subsidence, invasive species proliferation, and diminished biodiversity, while enabling agricultural output in the EAA that farmers argue justifies continued water allocations to sustain productivity and prevent economic disruption.[184] Preservation advocates counter that such diversions exacerbate long-term costs, including reduced natural flood mitigation and aquifer recharge, which restoration efforts aim to address.[3] The Comprehensive Everglades Restoration Plan (CERP), authorized by Congress in 2000, embodies ongoing debates by seeking to restore hydrologic conditions while maintaining water supplies for over 8 million urban residents and agricultural users, but implementation has faced opposition from development interests, notably the sugar industry, which has litigated against projects like the EAA Reservoir, claiming they infringe on water rights needed for irrigation and would impose undue economic burdens.[127][185] Federal courts, including the 11th Circuit in 2025, rejected these challenges, upholding reservoir construction to capture water previously discharged to ocean for Everglades flow, prioritizing ecological restoration over expanded agricultural claims.[186] Economic analyses of restoration yield mixed perspectives: industry sources emphasize agriculture's direct contributions, while independent estimates project net benefits of $46.5 billion in present value from enhanced ecosystem services like tourism and flood protection, potentially outweighing short-term development losses.[179][174] Full reversal of development impacts remains infeasible due to entrenched urban infrastructure and land subsidence, underscoring causal trade-offs where prior hydrological alterations preclude pristine restoration without sacrificing existing economic uses.[3]

Political and Scientific Disputes

Political disputes surrounding Everglades restoration have often centered on funding allocation and competing priorities between agricultural interests, urban water needs, and ecological recovery. The Comprehensive Everglades Restoration Plan (CERP), authorized by Congress in 2000, has faced criticism for chronic underfunding and delays, with federal contributions fluctuating based on partisan divides; for instance, in 2022, Florida Republicans expressed dissatisfaction with infrastructure law funds tied to state matching requirements, viewing them as federal overreach despite broad support for the $20+ billion project.[187] State-level tensions emerged in 2025 when Governor Ron DeSantis criticized the Florida House budget for allocating $279 million to restoration while allegedly underprioritizing other water projects, highlighting intra-party conflicts over fiscal emphasis.[188] Agricultural stakeholders, particularly the sugar industry, have resisted measures like land acquisition for storage reservoirs and stricter phosphorus controls, arguing that best management practices sufficiently mitigate runoff, while environmental groups push for federal lawsuits to enforce cleaner standards, as seen in ongoing litigation tracing back to 1990s disputes over nutrient pollution exceeding 10 parts per billion thresholds.[189][190] Scientific controversies have intertwined with these political battles, particularly regarding the efficacy of phosphorus reduction and the integration of ecological models into policy. Debates persist over whether current stormwater treatment areas adequately filter agricultural pollutants, with some studies questioning compliance claims; for example, a 2019 analysis linked Everglades-derived nutrients to coral degradation in Florida Bay, though industry-backed research contends levels meet legal benchmarks below state limits of 0.18 mg/L annually.[191][192] The 2023-2024 legal clash between the Everglades Foundation and former scientist Thomas van Lent exemplified tensions, where the nonprofit alleged theft of proprietary data on water quality modeling after van Lent publicly challenged optimistic restoration projections, raising questions about the politicization of scientific data in advocacy-driven research.[193][194] National Academies biennial reviews of CERP, including the 2024 assessment, acknowledge progress in hydrologic restoration—such as Tamiami Trail modifications increasing sheetflow by over 300 cubic feet per second—but criticize incomplete climate adaptation modeling and fragmented agency coordination, urging better incorporation of sea-level rise projections (up to 2 feet by 2060) that could alter peat soil stability and species distributions.[195][196] These disputes underscore broader causal realities: historical drainage engineering reduced natural water volumes by 40-50% since the 1900s, exacerbating vulnerabilities, yet restoration skeptics argue that empirical monitoring shows mixed ecosystem responses, with invasive species like Burmese pythons decimating mammal populations by 90% in some areas, complicating attribution of declines to restoration shortfalls versus external stressors.[141] Tribal groups, including the Miccosukee, have litigated against federal plans prioritizing urban flood control over traditional slough flows, as in challenges to Central Everglades projects that could inundate cultural sites.[197] Overall, while CERP has restored over 100,000 acres of wetlands by 2024, critics from both scientific and political spheres contend that vested interests— including philanthropic funding influencing research agendas—have slowed adaptive management grounded in verifiable hydrologic data.[198][199]

Climate Change and Adaptation Issues

Rising sea levels in the Greater Everglades have been measured at approximately 2.4 mm per year from 1993 to 2020, contributing to saltwater intrusion that elevates salinity in formerly freshwater marshes and triggers vegetation die-off.[200] This intrusion has led to observed peat soil collapse, with losses up to 1.1 meters in affected coastal areas, as elevated salinity kills sawgrass roots (Cladium jamaicense), reducing organic matter accumulation and accelerating subsidence.[200] [201] Such collapse equates to soil elevation deficits comparable to a decade of sea level rise in a single event, undermining the wetland's natural capacity to maintain elevation through peat buildup.[201] Vegetation shifts reflect these hydrologic changes, with mangrove forests expanding inland by an average of 3 kilometers since the 1940s, displacing sawgrass prairies and hardwood hammocks while altering habitat for species like wading birds.[202] However, ecosystem responses vary; while mangroves may enhance carbon sequestration in transitional zones, freshwater peat marshes exhibit reduced carbon storage due to decomposition under prolonged inundation and salinity stress.[203] These alterations compound pre-existing stressors from historical drainage, amplifying biodiversity losses in oligotrophic sloughs and tree islands. Adaptation strategies emphasize restoring natural freshwater flows to bolster resilience against salinity and inundation. The Comprehensive Everglades Restoration Plan (CERP), authorized in 2000, incorporates increased water storage and delivery to counteract intrusion, with projects like the C-111 Spreader Canal pump stations—operational since 2013—redirecting overland flow to Taylor Slough and preventing eastward drainage losses.[204] Additional measures include plugging canals at Cape Sable Seaside to halt artificial saltwater pathways and raising sections of the Tamiami Trail (U.S. 41) by up to 1 foot since 2000 to facilitate sheet flow into Shark River Slough.[204] These efforts aim to mimic pre-drainage hydrology, enabling peat accretion to potentially match moderate sea level rise rates observed to date. Challenges persist as projected sea level increases of 0.3 to 2.5 meters by 2100 could outpace restoration benefits, particularly if peat collapse reduces adaptive elevation gains and exacerbates flooding in low-lying areas.[200] Reduced freshwater inflows from upstream diversions limit the efficacy of structural fixes, while intensified hurricanes—linked to warmer Atlantic waters—threaten infrastructure and erode coastal buffers.[204] Long-term viability requires ongoing monitoring and flexible designs, such as elevated facilities at Flamingo developed post-2012 to withstand storm surges, but debates center on whether engineered interventions can fully offset accelerated relative rise driven by both eustatic and subsidence factors without broader watershed management.[204]

Ongoing Restoration Critiques and Efficacy

The Comprehensive Everglades Restoration Plan (CERP), enacted in 2000, has achieved accelerated implementation in recent years through record state and federal funding surges in 2022 and 2023, yielding hydrologic benefits such as increased freshwater flows into northeastern Everglades National Park and select large-scale ecosystem segments.[195] Nonetheless, the National Academies' tenth biennial review in 2024 critiqued the opacity of progress metrics, stating that data comparing actual outcomes to restoration expectations are "hard to find and interpret," hindering rigorous efficacy evaluations.[195] Independent analyses attribute this to historical underfunding, bureaucratic inertia, and inaccurate scheduling, which have collectively slowed system-wide recovery despite targeted gains in sheetflow and water distribution.[141] Project delays exemplify operational critiques; the Everglades Agricultural Area reservoir, intended to store and treat Lake Okeechobee discharges, faces completion deferral to 2034 due to protracted litigation and engineering setbacks, exacerbating urban water diversion issues.[205] Total CERP costs have escalated from an original $7.8 billion estimate to $23.2 billion (adjusted to 2019 dollars), driven by inflation, design revisions, and extended timelines, with federal expenditures reaching $3.2 billion and state contributions $2.8 billion through fiscal year 2024.[206] [128] These overruns underscore inefficiencies in adaptive management, described as "time-consuming and burdensome," which impede responsive adjustments to emerging data.[195] Efficacy remains partial, with hydrologic restorations like high-flow pulses in Shark River Slough enhancing wetland inundation patterns, yet undermined by persistent water quality shortfalls and invasive species proliferation.[207] Stormwater Treatment Areas have lowered phosphorus loads to near-compliance levels in monitored basins, but exceedances persist downstream, as CERP prioritizes flow volume and timing over comprehensive pollutant mitigation.[208] Invasives such as Burmese pythons and African jewelfish disrupt trophic structures, reducing native fish populations and energy transfer, thereby diminishing habitat recovery gains from water reallocations; these threats fall outside CERP's core scope, limiting holistic effectiveness.[209] [210] [211] Broader critiques highlight insufficient integration of climate drivers, including sea-level rise projected at 0.5–2 meters by 2100, which could salinize freshwater marshes and erode restoration hydrology without updated modeling.[195] The National Academies urges streamlined decision frameworks, routine climate scenario simulations, and incorporation of Miccosukee and Seminole tribal insights to bolster resilience, arguing that current approaches risk amplifying vulnerabilities in an already fragmented ecosystem.[195] While partial hydrologic and flood-control advances provide measurable value, unmitigated invasives and adaptive gaps indicate CERP's efficacy falls short of reversing pre-drainage dynamics, with ecosystem indicators showing stasis or decline in invasive-dominated zones.[212]

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