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Lake Lyndon B. Johnson
Lake Lyndon B. Johnson
from Wikipedia

Lake Lyndon B. Johnson (more commonly referred to as Lake LBJ and originally named Lake Granite Shoals) is a reservoir on the Colorado River in the Texas Hill Country about 45 miles northwest of Austin. The reservoir was formed in 1950 by the construction of Granite Shoals Dam by the Lower Colorado River Authority (LCRA). The Colorado River and the Llano River meet in the northern portion of the lake at Kingsland.

Key Information

Location and history

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Lake LBJ just east of Kingsland.

The towns of Granite Shoals, Kingsland, Horseshoe Bay, Highland Haven, and Sunrise Beach are located on the lake. The boundary line separating Burnet County and Llano County runs down the center of the lake.

The lake was originally called Lake Granite Shoals. The dam would be renamed Wirtz Dam in 1952 for Alvin J. Wirtz, the first general counsel of the LCRA, and the lake was renamed to Lake Lyndon B. Johnson in 1965 in honor of US President Lyndon Baines Johnson.[1] In addition to his work to enact the Rural Electrification Act that formed the basis for building the Texas Highland Lakes, President Johnson owned a ranch on the lake (which was separate and apart from the LBJ Ranch in Stonewall, Texas). He and Mrs. Johnson entertained national and foreign dignitaries on the lake during his vice presidency and presidency.

The other reservoirs on the Colorado River are Lake Buchanan, Inks Lake, Lake Marble Falls, Lake Travis, Lake Austin, and Lady Bird Lake. Lake LBJ along with Inks Lake and Lake Marble Falls are pass-through lakes for Lake Buchanan and Lake Travis. There is no room in Lake LBJ for additional water storage, and water that comes in must go out. Therefore, Lake LBJ is at a near constant level, but the level can fluctuate, especially during a flood. The LCRA lowers the lake periodically for maintenance on Wirtz Dam and to allow landowners to remove sediment around their docks.

Fish and wildlife populations

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Lake LBJ has been stocked with several species of fish intended to improve the utility of the reservoir for recreational fishing. Fish present in Lake LBJ include largemouth bass, white bass, catfish, and crappie. Lake LBJ is one of the Highland Lakes infested with hydrilla, a non-native aquatic plant species, and the LCRA is undergoing treatment to eradicate the hydrilla.

Recreational uses

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Aerial view of the Lake, looking north.

Most of the property bordering Lake LBJ is privately owned. The Nightengale Archaeological Center at Kingsland is a unique educational park operated by the Lower Colorado River Authority that is adjacent to Lake LBJ. The lake is also home to Camp Champions, the only summer camp with property on the lake[citation needed]. The popularity of Lake LBJ is largely due to its normally constant level water which provides ideal conditions for boating, water skiing, riding personal water craft and other water sports. Swimming in summer months is inadvisable due to the presence of the rare but deadly Naegleria fowleri.[2]

Cooling water

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The lake provides cooling water for the Thomas C. Ferguson Power Plant that is located on its shores.

See also

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References

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Revisions and contributorsEdit on WikipediaRead on Wikipedia
from Grokipedia

Lake Lyndon B. Johnson, commonly referred to as Lake LBJ, is a man-made located in Burnet and Llano counties, , approximately four miles west of Marble Falls on the where it converges with the .
Impounded by the Alvin J. Wirtz Dam—a and earthfill structure completed in 1951 by the (LCRA)—the reservoir was originally known as Lake Granite Shoals and serves primarily for hydroelectric power generation, with secondary roles in municipal and industrial and flood control as part of the Highland Lakes system. The dam, renamed in 1952 for LCRA advocate Alvin J. Wirtz, created a constant-level lake with a surface area of 6,273 acres, a storage capacity of 133,090 acre-feet at its conservation pool elevation of 825 feet above mean , and a maximum depth of 90 feet.
Renamed in 1965 to honor President , who supported LCRA initiatives during his political career, Lake LBJ features a of 36,290 square miles and approximately 200 miles of shoreline, fostering extensive recreational use including boating, fishing for species like and , and waterside development. Its stable water levels, with minimal annual fluctuations of 0 to 2 feet, distinguish it from upstream and downstream reservoirs in the chain, enhancing its appeal for residential communities and tourism in the .

Physical Geography

Location and Extent

Lake Lyndon B. Johnson is a reservoir on the in the , spanning primarily Burnet and Llano counties in , . It is impounded by Wirtz Dam, located four miles west of Marble Falls at coordinates 30°33′ N, 98°20′ W, and lies approximately 45 miles northwest of Austin. The reservoir covers a surface area of 6,273 acres at its normal operating elevation of 825.68 feet above mean and has a drainage area of 36,290 square miles, of which about 11,900 square miles are noncontributing. Its shoreline extends approximately 270 miles, much of which is bordered by residential and commercial development. The lake's extent is influenced by its role in the Lower Authority's chain of Highland Lakes, where it maintains relatively constant levels for and compared to upstream and downstream reservoirs.

Reservoir Characteristics and Hydrology

Lake Lyndon B. Johnson, impounded by Alvin Wirtz Dam on the in , maintains a conservation storage capacity of 133,090 acre-feet at its normal operating elevation of 825.68 feet above mean . At this elevation, the reservoir spans a surface area of 6,273 acres, with a contributing of 36,290 square miles that includes both contributing and non-contributing sub-basins. The lake's shoreline extends approximately 270 miles, bordering a mix of residential, commercial, and undeveloped lands. Maximum depths reach up to 90 feet in portions near the dam, though average depths are shallower due to the reservoir's relatively flat and sediment accumulation. Hydrologically, inflows to Lake Lyndon B. Johnson derive mainly from regulated discharges from upstream Lakes Buchanan and , augmented by unregulated tributary flows from the , which converges with the at the reservoir's northern extent. The (LCRA) manages outflows through Wirtz Dam's hydroelectric turbines and spillways, prioritizing power generation, downstream , and flood mitigation within the interconnected Highland Lakes system. Water levels typically hover near the 825-foot conservation pool but fluctuate with seasonal precipitation, upstream releases, and operational needs; for instance, levels were recorded at 824.72 feet on October 27, 2025. Periodic drawdowns below full pool occur for dam maintenance and sediment management around private docks, reflecting the reservoir's operational balance between storage reliability and infrastructure upkeep. The reservoir's dead pool storage stands at 18,840 acre-feet below elevation 793.40 feet, underscoring vulnerability to prolonged droughts in the semi-arid , where losses exceed direct inflows during dry periods. Historical extremes include a record high of 836.2 feet on , 1952, driven by intense upstream rainfall and runoff. surveys indicate gradual capacity loss, with the 2020 assessment validating conservation pool volumes within ±6.23% of prior estimates, attributable to ongoing deposition from riverine sediments.

History and Construction

Planning and Dam Building

The (LCRA), established in 1934 to harness the for flood control, hydroelectric power, and , planned the Granite Shoals Dam in the mid-1940s as the final major addition to its Highland Lakes chain. This expansion addressed growing electricity demands in post-World War II and aimed to regulate downstream flows more effectively after completing upstream reservoirs like in 1942. The project focused on generating additional hydropower while providing storage for municipal and agricultural water needs in counties. Construction of the , a combined concrete gravity and earthfill embankment structure spanning the in Burnet and Llano counties, began on September 15, 1948. The work proceeded alongside the simultaneous building of Starcke Dam downstream to create Lake Marble Falls, enabling coordinated reservoir operations. Deliberate impoundment started in early 1950 to form the initial pool, with the dam reaching full operational height of approximately 118 feet and completing powerhouse integration by November 1951. The structure included gates and turbines designed for peaking power output, contributing to LCRA's grid reliability without federal funding, relying instead on revenue bonds. Upon completion, the reservoir, initially named Lake Granite Shoals, extended about 40 miles upstream toward , inundating approximately 16,920 acres at normal pool elevation with a storage capacity of 354,000 acre-feet dedicated primarily to power generation. The marked the culmination of LCRA's dam-building , shifting focus thereafter to and operations rather than new construction.

Naming and Post-Construction Development

The reservoir, originally known as Granite Shoals Lake upon its completion in 1951, was renamed Lake Lyndon B. Johnson on April 22, 1965, to honor President Lyndon B. Johnson's efforts in securing federal funding for the Lower Authority's Highland Lakes system. This renaming reflected Johnson's advocacy for regional water infrastructure during his tenure as a Texas congressman and senator, which supported the authority's projects despite initial opposition from federal agencies concerned about flood control priorities. The initiative gained momentum in early 1965 when the Kingsland unanimously endorsed the change, aligning with broader tributes to Johnson's presidency. Following impoundment behind Wirtz Dam, which began generating hydroelectric power on June 27, 1951, the lake spurred residential and recreational development in adjacent communities. Areas like Granite Shoals emerged as early lake resorts focused on fishing cabins and seasonal , transforming rural landscapes into accessible waterfront destinations. Kingsland, previously a modest settlement, underwent economic revitalization through expanded facilities, marinas, and , leveraging the lake's 6,280 acres for water-based activities that boosted local . Subsequent decades saw sustained growth in luxury waterfront properties and subdivisions, particularly in Horseshoe Bay and surrounding Hill Country locales, where custom home construction emphasized lakefront access and amenities like golf courses overlooking the reservoir. By the 2020s, development accelerated with projects such as new residential communities and infrastructure upgrades, including bridge improvements, to accommodate rising demand for second homes and retiree relocations amid Texas's population influx. This expansion has been driven by the lake's stable water levels managed by the Lower Colorado River Authority, enabling reliable recreational use and property values exceeding multimillion dollars for prime sites.

Operational Management

Hydropower and Water Supply

The Wirtz Dam, which impounds Lake Lyndon B. Johnson, features two hydroelectric turbines with a combined generating capacity of 60 megawatts, enabling the production of renewable electricity primarily during periods of sufficient inflow from the . Constructed between 1949 and 1951, the dam's power plant operates by releasing water through the turbines, with outflows typically limited to power generation except during flood events when spillways are utilized. The (LCRA), which manages the facility, integrates this output into the regional grid, contributing to Texas's baseload and peaking power needs without reliance on fossil fuels. While Lake Lyndon B. Johnson's storage capacity of approximately 138,500 acre-feet supports operational flexibility, its primary role in water supply is subordinate to upstream reservoirs like Lakes Buchanan and Travis, which serve as the Highland Lakes system's main sources for municipal, agricultural, and industrial demands. LCRA coordinates releases from the lake to maintain downstream flows for water users along the lower , but the reservoir's relatively low storage volume—compared to the over 2 million acre-feet combined in the upper lakes—limits its direct contribution to long-term supply, focusing instead on real-time regulation and flood mitigation. and operational drawdowns further constrain its utility for sustained water provisioning, with LCRA prioritizing conservation measures across the chain to balance , cooling needs, and regional allocations.

Industrial Uses Including Cooling

Lake Lyndon B. Johnson functions primarily as a cooling for the Thomas C. Ferguson Power Plant, a natural gas-fired combined cycle facility operated by the (LCRA) and located near Horseshoe Bay in . The plant, with a net maximum capacity of approximately 556 megawatts, draws water from the lake for condenser cooling to manage thermal output during . This use aligns with the lake's design as a constant-level , enabling reliable once-through or recirculated cooling operations that minimize fluctuations in water levels compared to upstream storage lakes. Under water rights adjudicated in Certificate No. 14-5480 (dated June 28, 1989), the LCRA holds authorization to impound up to 138,500 acre-feet in Lake LBJ and to divert, circulate, and recirculate water specifically for industrial purposes, including power plant cooling at the Ferguson facility, with a priority date of August 24, 1970, for such diversions. Consumptive use is limited to 15,700 acre-feet per year, primarily accounting for evaporative losses associated with the cooling process. The plant's operations, which include a 2014 upgrade enhancing efficiency, integrate this cooling draw with the lake's hydroelectric functions at Wirtz Dam, where controlled releases support both power generation and thermal management without significantly depleting downstream flows. Beyond power generation cooling, Lake LBJ supports limited ancillary industrial needs within the LCRA , though these are subordinate to its roles in and ; no major manufacturing or other non-utility industrial withdrawals are documented as primary users. The integration of cooling underscores the reservoir's engineered multipurpose utility, balancing energy production demands with regional management constraints.

Ecology and Biodiversity

Fish and Wildlife Populations

The fish community in Lake Lyndon B. Johnson consists primarily of sportfish and prey species, with populations monitored through periodic surveys by the (TPWD). (Micropterus salmoides) exhibit moderate abundance, with electrofishing catch rates in 2020 averaging 45 fish per hour of effort, reflecting stable recruitment supported by available in the reservoir's riverine and lentic zones. (Micropterus treculii), a , also occur at moderate densities, though their populations are influenced by hybridization risks with introduced in the basin. (Morone chrysops) maintain a moderate population with seasonal spawning runs up tributaries, but gill netting in 2021 indicated lower relative abundance compared to historical levels. Catfish species dominate the angling catch, with (Ictalurus punctatus) showing increased catch rates in the 2020 survey, reaching 12 per hour, attributed to natural reproduction and supplemental stocking efforts. (Ictalurus furcatus) are abundant in deeper s, contributing to a robust predator base that regulates prey dynamics. , particularly (Pomoxis annularis), support excellent populations, with recent fishing reports noting fair to good catches in 15-20 feet of on structures using minnows or jigs as of October 2022. Prey species such as (Lepomis macrochirus), gizzard shad (Dorosoma cepedianum), and (Lepomis auritus) form the base of the , with gizzard shad providing essential forage for predatory ; (Dorosoma petenense) presence enhances larval survival but can fluctuate with temperatures. TPWD has implemented stocking programs to bolster sportfish populations, including periodic releases of and (Oncorhynchus mykiss) in adjacent state park areas, though the reservoir's primary productivity sustains self-reproducing communities without heavy reliance on introductions. Invasive species like zebra mussels (Dreissena polymorpha), detected in 2019, pose risks to native fish by altering dynamics and substrate availability, potentially reducing forage for filter-feeding . Terrestrial wildlife around the reservoir includes abundant (Odocoileus virginianus), which utilize riparian zones for foraging and fawning, with local observations indicating frequent sightings of bucks, does, and fawns near shorelines. (Canis latrans) and populations (Vulpes spp.) are common predators in the surrounding Hill Country habitat, preying on smaller mammals and influencing deer through control of herbivores. Avian is high, with eBird records documenting over 130 native and naturalized birds, including waterfowl like Canada geese (Branta canadensis) and raptors such as great horned owls (Bubo virginianus), supported by the lake's emergent vegetation and adjacent grasslands. These populations benefit from the reservoir's but face pressures from urban development and recreational activities in the basin.

Water Quality Dynamics

Water quality in Lake Lyndon B. Johnson is monitored by the Texas Commission on Environmental Quality (TCEQ) and the (LCRA), with assessments based on parameters including dissolved oxygen (DO), , chlorophyll-a, bacteria, and algal toxins. According to the 2022 TCEQ Integrated Report for Basin 14, the lake fully supports designated uses for aquatic life, domestic , , and general use, with no exceedances for DO minima (3 mg/L), (mean 0.09-0.34 mg/L below 10 mg/L criterion), E. coli geometric means (1.76-59.41 MPN/100mL below 126 criterion), (6.5-9), and (mean 281-329 mg/L below 400 mg/L). However, it does not support reservoir criteria due to excessive algal growth, classified as an impairment under Category 5c, driven by enrichment rather than specific exceedances in total phosphorus (mean 0.69 mg/L) or chlorophyll-a (14.1 µg/L). Seasonal dynamics are influenced by thermal stratification, which depresses DO in deeper waters during summer stagnation, with historical lows linked to water column mixing and a documented of 498 individuals on , 1996. conditions exacerbate , as observed in reservoirs where Lake LBJ shifted to eutrophic status during low-inflow periods, increasing algal productivity due to concentrated s from upstream agricultural and sources. LCRA models simulate these trends, incorporating , point-source discharges, and atmospheric inputs to predict DO sags and , with the lake's run-of-river characteristics maintaining relatively constant levels (824.40-825 ft elevation) but limiting dilution during dry spells. Algal monitoring reveals periodic risks, with LCRA testing for in Lake LBJ and adjacent Highland Lakes; no harmful concentrations were detected in samples from 2022 to 2024, though toxins accumulate in algal mats, posing contact hazards. Flood events, such as those in July 2025, temporarily elevate bacteria and from runoff and debris, prompting advisories for avoidance of murky areas, but levels normalize within days to weeks under flushing flows. Overall, while core parameters remain within standards, nutrient-driven algal dynamics reflect basin-wide pressures, with management focused on inflow regulation and source controls to mitigate episodic impairments.

Recreational Utilization

Primary Activities and Access

The primary recreational activities on Lake Lyndon B. Johnson center on water-based pursuits, including , , , and watersports such as jet skiing and . The reservoir's design maintains a relatively constant water level year-round, unlike many lakes subject to significant fluctuations, enabling consistent access for these activities. Boating predominates due to the lake's navigable stretches from Kingsland to Horseshoe Bay, supported by developed shorelines featuring bulkheads and boathouses that provide shelter for vessels. Public access to the lake is facilitated through multiple boat ramps, marinas, and parks managed by entities including the (LCRA) and local operators. Key public ramps include those at Granite Beach Recreation Area and Lake LBJ Yacht Club and Marina, which charge a launch fee and offer parking for 20-30 trailers. Additional ramps are located in Cottonwood Shores and Kingsland, providing easy entry points for boaters. Six marinas around the lake supply boat slips, dry storage, and rentals for pontoons and kayaks, enhancing accessibility for recreational users. Shoreline parks, such as those with fishing piers, swimming areas, and picnic facilities, further support non-boating activities like and picnicking. These sites, often tree-shaded and waterfront, include amenities like covered pavilions and are open to the public, though some require entrance fees or passes. The lake remains publicly accessible overall, with no broad restrictions on entry beyond standard operational rules from LCRA.

Safety Considerations and Regulations

Boating on Lake Lyndon B. Johnson is governed by state laws and local ordinances enforced by entities including the (TPWD) and the (LCRA). Operators born on or after September 1, 1993, must complete a boater education course to operate motorized vessels exceeding 15 horsepower. Children under 13 years old are required to wear a U.S. Coast Guard-approved life jacket at all times while aboard, and all passengers must have access to properly fitted life jackets. No person under 14 years may operate a boat or without direct supervision by a qualified adult. Reckless operation, including excessive speed or operating under the influence, is prohibited, with no-wake zones enforced near marinas, docks, and swimming areas to prevent accidents in high-traffic periods like weekends and holidays. Swimming safety emphasizes avoiding isolation and inherent hazards of unchlorinated reservoir water. Swimmers should never enter alone, wear life jackets if non-proficient, and restrict activities to designated areas, excluding zones within 50 feet of public boat ramps. Post-flood conditions pose elevated risks from submerged , fast currents, and bacterial proliferation in murky or stagnant water, prompting LCRA advisories to avoid lakes entirely during such events and to steer clear of cloudy, smelly, or algae-laden sections thereafter. Rare but severe threats include , a free-living linked to primary amebic , with documented fatalities in lakes; preventive measures include plugging the nose during submersion and avoiding warm, sediment-disturbed waters. Invasive species regulations mandate cleaning, draining, and drying all vessels, trailers, livewells, and gear upon leaving the lake to curb spread, a legal requirement under law prohibiting their transport. LCRA and TPWD report 10 incidents on Lake LBJ in 2024, resulting in 7 injuries but no fatalities, underscoring persistent risks despite regulations; historical data shows multiple drownings in prior years, such as three by mid-2019, often tied to inadequate life jacket use or impairment. and channel markers aid , with tampering illegal and reporting urged to LCRA for .

Economic and Societal Impacts

Local Economic Contributions

The supports substantial local economic activity primarily through and , with visitor spending in 2011 generating $122.5 million directly across the Upper Highland Lakes chain, including Lake LBJ, and yielding a total economic output of $185.5 million while supporting 3,648 jobs inclusive of multiplier effects. Lake LBJ contributes disproportionately to this, hosting 63.9% of the region's capacity and driving the majority of lake-related occupancy revenues, which exceeded $1 million annually in state taxes from such properties alone. Activities such as , , and waterfront lodging sustain , operations, and retail businesses in adjacent counties like Burnet and Llano, where lake-related accounted for $117.8 million in total economic activity and 2,721 jobs in Llano County during the same period. Elevated property values further bolster local tax bases and real estate sectors, with lakefront homes on Lake LBJ averaging 3.5 times the county-wide home value and lake-related properties comprising 46.7% of total taxable value despite occupying only 1.9% of land area. In 2011, the taxable value of properties around Lake LBJ reached $1,092.8 million in Burnet County and $1,475.1 million in Llano County, funding public services and infrastructure. Seasonal demand enhances rental yields for waterfront investments, with high occupancy rates for vacation properties reflecting sustained visitor interest from nearby urban centers like Austin. The lake's development since its impoundment in 1951 by the has catalyzed broader regional growth, converting arid Hill Country terrain into a recreational economy hub that attracts out-of-area spending and counters rural depopulation trends. State and local tax receipts from these activities totaled $9.6 million in 2011, with lake-related portions supporting $2.6 million in local taxes and $7 million in state taxes, underscoring the reservoir's role in fiscal stability for host communities.

Environmental Trade-offs and Challenges

The construction of Lake Lyndon B. Johnson in 1967 inundated approximately 16,625 acres of riparian and upland habitat along the , fragmenting ecosystems and displacing native and adapted to free-flowing river conditions. This trade-off enabled generation, flood control, and water storage benefiting downstream users, but permanently altered migratory bird routes, fish spawning grounds, and terrestrial wildlife corridors in the . Ongoing water level fluctuations managed by the for operational needs further stress riparian zones, reducing vegetation diversity and exacerbating in shallow coves. Sedimentation poses a persistent challenge, with a 2020 volumetric survey by the Water Development Board revealing accumulated deposits reducing usable storage capacity by an estimated 5-10% since impoundment, primarily from sandy inflows and watershed . Pre-impoundment complicates precise loss calculations due to layered in cores, but annual deposition rates mirror broader Highland Lakes trends of 400+ acre-feet, threatening long-term viability and necessitating debates that pit restoration against industrial extraction interests. Flood events, such as those in July 2025, resuspend sediments, elevating and fostering anaerobic conditions that harm benthic organisms. Water quality degradation stems from eutrophic conditions documented in EPA assessments, where nutrient loading from agricultural runoff and upstream releases promotes overgrowth, with levels exceeding safe thresholds in Lake LBJ during 2023 blooms, endangering human and pet health. Routine LCRA monitoring confirms recurrent harmful in the Highland chain, exacerbated by drought-induced stagnation that shifted LBJ toward mesoeutrophy in 2011-2015 studies. Post-flood spikes, including potential pathogens in stirred sediments, compound risks, as unchlorinated reservoir dynamics inherently support microbial proliferation absent in treated pools. Invasive species amplify ecological pressures, with zebra mussels established since 2019, rapidly colonizing substrates and outcompeting natives by filtering , which disrupts food webs and clogs intake structures for utilities. Their veligers spread via boating traffic, infesting 27 lakes by 2021 and posing threats valued at millions in mitigation costs. Submerged aquatic plants like have proliferated since 2023, forming dense mats that alter oxygen levels, hinder navigation, and outshade native vegetation, requiring mechanical removal that disturbs sediments further. These invasives underscore a trade-off of connectivity facilitating unintended introductions against the isolation benefits of unaltered rivers.

References

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