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Merced River

The Merced River is a westward-flowing tributary of the originating on the south side of Mount Lyell in the at an elevation of 13,114 feet and descending through before reaching its confluence in California's Central Valley. Its course traverses glacially sculpted canyons, alpine meadows, and , where it supports exceptional scenic, geological, and recreational values as a designated National Wild and Scenic River since 1987. The river's watershed, spanning about 1,300 square miles, drains primarily within and adjacent lands, contributing to regional with average flows around 355 cubic feet per second at key monitoring points like Happy Isles. Ecologically, the Merced sustains diverse native and endemic species, including trout populations and amphibians like the limestone salamander, while its free-flowing segments preserve pristine fisheries amid ongoing restoration efforts to mitigate human-induced alterations such as channelization and flood damage. Below the park, the river faces modifications including dams like New Exchequer Dam forming Lake McClure for and flood control, which interrupt its natural flow and spark debates over water allocation between agricultural demands and environmental preservation. Designated segments emphasize wild characteristics upstream, transitioning to recreational uses downstream, underscoring the river's role in balancing conservation with and needs in a water-scarce region.

Physical Characteristics

Course and Hydrology

The Merced River originates on the south side of in at an elevation of 13,114 feet (3,998 m), where its headwaters form from several forks including the Red Peak Fork, Merced Peak Fork, Triple Peak Fork, and Lyell Fork. These upper reaches flow northwest through glacially carved terrain, descending through steep canyons and passing features such as and before entering Little Yosemite Valley and subsequently broadening into the floor of . The river's total length measures 145 miles (233 km). Upon exiting near El Portal, the Merced River enters a narrow, steep-sided gorge with an average gradient of 70 feet per mile (13 m/km), receiving inflows from principal tributaries such as Illilouette Creek, Tenaya Creek, Yosemite Creek, Echo Creek, and Sunrise Creek within the park, and the larger South Fork Merced River downstream near Briceburg. The South Fork, the river's largest tributary at 43 miles (69 km) long, drains Yosemite's southern watersheds including Wawona. Beyond the gorge, the river traverses foothills regulated by structures like the Crocker-Huffman Diversion Dam before impounding in Lake McClure behind New Exchequer Dam at approximately 900 feet (274 m) elevation. In its lower course, the Merced River flows past Merced Falls Dam and across the floor, where it is joined by minor tributaries like Dry Creek, before reaching its mouth at the near Stevinson in Merced County. The Merced River's watershed spans 1,266 square miles (3,280 km²), with elevations ranging from 52 feet (16 m) at the valley floor to 13,090 feet (3,990 m) in the headwaters, primarily fed by snowmelt leading to peak discharges in spring and early summer. Flows are heavily regulated by reservoirs including Lake McClure for , via the Merced Irrigation District, , and , which attenuate natural peaks and sustain baseflows; for instance, USGS gauges record maximum discharges exceeding 10,000 cubic feet per second (cfs) during floods at upper sites like Happy Isles.

Watershed

The Merced River watershed encompasses approximately 1,280 square miles (3,300 km²) on the western slope of the central in , draining portions of , Madera, and Merced counties before joining the . Elevations within the basin range from about 52 feet (16 m) near the river's mouth to over 13,000 feet (4,000 m) at the headwaters. The watershed is bordered to the north by the basin and to the south by the upper drainage, with the upper portion largely within and . Major tributaries include the South Fork Merced River, the largest contributor originating in Yosemite National Park near Wawona and joining the main stem below Yosemite Valley; the North Fork Merced River; and upper branches such as the Triple Peak Fork, Lyell Fork, Red Peak Fork, Illilouette Creek, Tenaya Creek, Yosemite Creek, Bridalveil Creek, and Poohoo Creek. Lower tributaries like Dry Creek add drainage from the surrounding foothills before the river reaches the Central Valley. These tributaries collectively supply snowmelt-dominated flows, with the basin's hydrology driven by seasonal precipitation ranging from heavy winter snowpack in the high Sierra to rainfall in the lower elevations. Land cover in the watershed varies markedly by elevation and location: the upper basin, comprising about 30% of the area within , consists primarily of granitic terrain, coniferous forests, alpine meadows, and protected wilderness with minimal human modification. In contrast, the lower watershed transitions to foothill oak woodlands and intensive agricultural lands in the , including croplands for almonds, tomatoes, and dairy operations, alongside urban development around Merced city. This downstream predominance of influences and , with historical and current farming contributing to nutrient loading despite upstream protections. Overall, the basin's undeveloped headwaters provide high-quality , while pressures in the valley necessitate management for and .

Geology

The Merced River traverses the , predominantly over granitic rocks intruded during the period approximately 80 to 130 million years ago, when from subducting oceanic plates beneath the North American continent crystallized into coarse-grained plutons composed mainly of , feldspar, and . These intrusions occurred into older and metamorphic basement rocks, fragments of which sporadically along the river's course, particularly in the steep walls of the Merced Gorge east of El Portal where metavolcanic and metasedimentary sequences date back over 500 million years. The river's upper reaches in the high expose fresh and variants, while downstream segments incorporate glacial and derived from of these resistant lithologies, forming sandy-loam textured deposits in broader valleys. Yosemite Valley, through which the Merced flows centrally, exemplifies combined fluvial and glacial modification of this granitic terrain, with the river's pre-glacial antecedent drainage deepened by multiple Pleistocene glaciations that amplified U-shaped cross-profiles and hanging valleys via ice abrasion and plucking. The trunk , advancing from the crest, scoured the valley floor to depths exceeding 2,000 feet in places, depositing moraines and erratics while overtopping features like Vernal and Nevada Falls; subsequent fluvial incision by the river has since excavated stair-step cascades and potholes in the bedrock. Post-glacial retreat around 16,000 years ago initiated meandering in the alluvial reach from Happy Isles to the valley's west end, where the river maintains a dynamic, mid-elevation amid exfoliated and sheer cliffs shaped by joint-controlled fracturing and unloading. Tectonic uplift of the , driven by isostatic rebound following Late erosion and faulting along its eastern escarpment, elevated the Merced's watershed to over 13,000 feet at its headwaters near Mount Lyell, enhancing gradient-driven downcutting that predates heavy glaciation. Evidence from drainage patterns suggests pre-glacial reorganization contributed to initial valley incision, with the river's path stabilizing through granitic resistance that preserves landforms like the upper Merced Canyon's 2,000-foot-deep, narrow trench. In the lower basin, the river crosses Pleistocene terrace deposits and , reflecting ongoing from Sierra-derived sediments amid regional in the Great Valley.

Ecology and Biology

Flora and Fauna

The Merced River's riparian corridors and associated s support diverse vegetation adapted to periodic flooding and high groundwater levels, including shrubs and trees that stabilize banks and provide habitat connectivity. Key riparian species include the rare Sierra sweet bay (Myrica hartwegii), which occurs exclusively on downstream sand bars and riverbanks from Wawona southward. Endangered and rare plants in the encompass Merced clarkia (Clarkia lingulata), a state-listed endangered annual herb; Yosemite onion (Allium yosemitense); Congdon’s wooly sunflower (Eriophyllum congdonii); Congdon’s lewisia (Lewisia congdonii); and shaggyhair lupine (Lupinus spectabilis), the latter near Lake McClure. These species thrive in edges and habitats influenced by river dynamics, though visitor trampling and erosion have degraded some areas. Aquatic and semi-aquatic fauna in the Merced River include native fish confined to lower reaches below approximately 4,000 feet elevation due to natural waterfalls blocking upstream migration, such as California roach (Hesperoleucus symmetricus), Sacramento pikeminnow (Ptychocheilus grandis), hardhead (Myllokunmingia sikanniensis), and riffle sculpin (Cottus gulosus). Introduced non-native species, including rainbow trout (Oncorhynchus mykiss), brown trout (Salmo trutta), brook trout (Salvelinus fontinalis), smallmouth bass (Micropterus dolomieu), and bluegill (Lepomis macrochirus), have been stocked historically since 1877, totaling over 33 million fish by 1990, altering native ecosystems through competition and predation. The federally threatened Central Valley Distinct Population Segment of steelhead (Oncorhynchus mykiss) persists in lower watershed segments, dependent on unimpeded flows for spawning. Amphibians tied to the river include the endemic limestone salamander (Hydromantes brunus), restricted to limestone outcrops in the Merced River canyon with only 15 known populations, eight protected under the Wild and Scenic Rivers Act. Riparian zones also sustain riparian-dependent reptiles and amphibians, though some like the foothill yellow-legged frog have been locally extirpated. Terrestrial mammals utilizing riverine habitats include (Odocoileus hemionus), which forage in meadows and riparian edges, alongside general Yosemite species like black bears (Ursus americanus) that access water and forage along the corridor. Avian diversity features over 260 species park-wide, with riparian specialists such as bald eagles (Haliaeetus leucocephalus) nesting along the Merced, great gray owls (Strix nebulosa), and peregrine falcons (Falco peregrinus), supported by the river's prey base including fish and . Rare bats like the spotted bat (Euderma maculatum) inhabit meadow-riparian interfaces. Overall, the ecosystem hosts nearly all 200 bird species and diverse vertebrates reliant on connectivity.

Ecological Dynamics and Threats

The Merced River's ecological dynamics are driven by its seasonal hydrology, with high spring snowmelt flows fostering sediment deposition, channel migration, and riparian habitat renewal, while low summer baseflows concentrate aquatic productivity in pools and riffles supporting invertebrate communities that form the base of the for fish like (Oncorhynchus tshawytscha). These processes sustain fall-run Chinook salmon populations in the lower watershed, where adults spawn in gravel beds during October–December, relying on pulse flows for egg incubation and juvenile rearing amid cooler, oxygenated waters. Riparian vegetation, including willows and cottonwoods, responds to flood pulses by colonizing inner bends, stabilizing banks and providing shade that moderates water temperatures critical for salmonid survival, though restoration sites show reduced undercut banks and woody debris compared to unaltered Central Valley streams, limiting overhead cover and prey availability. Threats to these dynamics primarily stem from upstream dams and diversions, such as those operated by the Merced Irrigation District, which reduce peak flows by up to 50–70% below natural levels, fragmenting and elevating summer water temperatures above 20°C, lethal thresholds for juvenile rearing and migration. Low flows during droughts, as in 2022 when sections ran dry, exacerbate of spawning gravels and strand juveniles, while historical and failures have degraded complexity, reducing side-channel habitats essential for refugia. Water quality impairments include elevated , , and nutrients from agricultural runoff and discharges, with incidents like the 2023 Gallo winery spill of 90,000 gallons contributing to localized spikes that stress aquatic biota. Climate-driven shifts, including reduced snowpack, intensify these pressures by shortening high-flow periods needed for scour and gravel recruitment, potentially collapsing runs without adaptive flow management.

History

Geological and Prehistoric Formation

The Merced River's geological formation is tied to the tectonic evolution of the , where uplift initiated around 10 million years ago during the , elevating the range and enabling river downcutting into granitic bedrock primarily formed 85 to 105 million years ago in the period. Prior to major glaciations, the ancestral Merced River incised a proto-valley through pre-glacial , accelerated by westward tilting of the approximately 5 million years ago and structural weaknesses like joints, with evidence indicating significant deepening occurred before Pleistocene ice ages. During the Pleistocene, multiple glaciations profoundly shaped the river's course, as alpine glaciers originating in the high advanced down the Merced canyon, eroding U-shaped valleys, cirques, and stair-step cascades while depositing moraines and till; key stages include the Sherwin (pre-700,000 years ago), Tahoe (~150,000–130,000 years ago), Tenaya, and the most recent Tioga glaciation, which reached its maximum extent 15,000 to 20,000 years ago. The Tioga advance filled to depths of up to 1,200 meters, with a trunk extending from the river's headwaters through the valley and beyond, overtopping features like Vernal and Falls; post-glacial isostatic rebound and continued fluvial by the Merced have since refined the , maintaining the river's path along glacial troughs and fracture-guided channels. Prehistoric sedimentary records along the lower Merced, such as Pliocene-Pleistocene deposits, reflect the river's role in basin filling and incision, with units like the Merced Formation documenting shifting depositional environments amid ongoing tectonic and climatic influences.

and Early Human Use

The Southern , particularly the Ahwahneechee subgroup in , maintained continuous occupation along the Merced River for approximately 4,000 to 5,500 years prior to European contact, with archaeological evidence of broader human presence in the Yosemite region dating back nearly 10,000 years, including hunting with spears and atlatls and seed processing on grinding stones. In the Merced River canyon near El Portal, sites indicate habitation as early as 9,500 years ago, reflecting adaptation to the river's riparian zones for settlement and resource extraction. These groups, sometimes incorporating elements, established villages directly along the riverbanks, constructing conical lodges known as umachas from bark and poles, with sites such as Wakalmata named for the Merced itself, termed Wa-kal-la meaning simply "the river" in their . Indigenous use centered on the river's ecological productivity, with fishing for migratory salmon (Oncorhynchus spp.) and steelhead (Oncorhynchus mykiss) that ascended unimpeded to Yosemite Valley and Wawona, supporting family-based fishing camps and weirs documented in pre-contact patterns and later treaty-era accounts. Settlements exploited the river for transportation via canoes or foot trails, water supply, and gathering of aquatic plants, while seasonal migrations shifted populations downslope to the milder Merced canyon in winter for fishing and hunting, contrasting summer uplands for acorn processing and big game. Landscape management through low-intensity fires maintained open oak savannas near the river, enhancing visibility for hunting deer and facilitating acorn harvests critical to Miwok diet, with obsidian tools traded from Mono neighbors aiding riverine activities like fish spearing. Lower reaches of the Merced, in the Central Valley foothills, saw complementary use by bands, who settled along rivers for similar fishing and irrigation-dependent gathering, though influence dominated the upper watershed. These practices sustained populations estimated in the hundreds per valley group, reliant on the river's for seasonal floods that enriched floodplains, without evidence of large-scale alteration prior to contact.

European Exploration and Modern Settlement

The first documented European expeditions into the Merced River region occurred during the Spanish colonial period, with Lieutenant Gabriel Moraga leading a party eastward from the toward the foothills in the fall of 1806, approaching but not fully entering the Yosemite area. Earlier Spanish missionary efforts in 1806 also advanced a half-day's march up the Merced River from the Central Valley, mapping terrain amid for potential sites, though these incursions remained limited and did not lead to permanent outposts. American exploration intensified after the 1848 California Gold Rush, with fur trappers like Joseph Reddeford Walker potentially viewing from afar during his 1833 Sierra Nevada crossing, though he did not descend into it. The first confirmed entry by into occurred on March 27, 1851, when the Battalion, a volunteer led by James D. , pursued Ahwahneechee Indians up the river's South Fork amid escalating conflicts following Native raids on settlements. , who had established trading posts along the Merced River as early as —including at the mouth of Piney Creek and the South Fork—facilitated these contacts, which displaced populations and opened the upper to further incursion. Settlement accelerated in the 1850s, driven by placer mining along the river's lower reaches and tributaries, with towns like Snelling and Merced Falls emerging as hubs for both white prospectors and displaced Native groups; by 1851, approximately 695 Indians resided near Merced Falls amid mixed communities. Erastus Kelsey settled near Merced Falls in 1853, securing one of the county's earliest water rights for mining and ranching, exemplifying the riparian claims that underpinned expansion. Toll roads, such as the 1856 route built by Milton and Houston Mann up the South Fork Merced, connected these sites to Yosemite Valley, boosting access for loggers and early tourists. By the late 19th century, railroads extended along the Merced Canyon, supporting mining, timber extraction, and tourism while enabling agricultural colonization in the Central Valley floodplain. Modern settlement patterns solidified with irrigation development, as the Robla Canal Company formed in the mid-1880s to divert Merced waters for farming, leading to the 's establishment in 1919 and transforming the lower river into a agricultural corridor with colonies like Hilmar (1901) near the river's mouth. These efforts, rooted in Gold Rush-era and water appropriation, shifted the region from transient camps to permanent agro-industrial communities, with the river serving as a vital axis for transport, precursors, and flood-prone valley reclamation.

Human Modifications and Engineering

Dams, Reservoirs, and Hydropower

The primary dams on the Merced River are operated by the Merced Irrigation District (MID) to support irrigation diversions, seasonal water storage, flood attenuation, and hydroelectric generation. These structures, concentrated in the lower river below Yosemite National Park, include the New Exchequer Dam, McSwain Dam, and Merced Falls Dam, which collectively form the core of the Merced River Hydroelectric Project (FERC Project No. 2179) and the separate Merced Falls Hydroelectric Project (FERC Project No. 2467). The projects generate power through run-of-river and storage operations, with combined installed capacity exceeding 100 megawatts, primarily from turbine facilities at the dams. ![Cascades Diversion Dam on the Merced River][float-right] The New Exchequer Dam, a 490-foot-high concrete-faced rock-fill structure completed in 1967, impounds Lake McClure, the river's largest reservoir with a storage capacity of 1,024,600 acre-feet. Construction began in 1964 and replaced the original Dam (built in 1926 with 281,200 acre-feet capacity), expanding storage to manage seasonal flows from the 1,276-square-mile for downstream and production. The associated Exchequer Powerhouse, located at the dam, has a generating capacity of 94.5 megawatts, utilizing water released through four turbines. Downstream, the McSwain Dam, an 80-foot-high embankment structure built as a regulating shortly after New , forms Lake McSwain with 9,730 acre-feet of storage to stabilize outflows for power generation and releases. It includes a powerhouse contributing to the project's total capacity of 103.5 megawatts across both facilities. Further downstream at river mile 55, the Merced Falls Dam maintains a small 65-acre impoundment with 678 acre-feet storage and generates 3.4 megawatts via a single development, focusing on diversion to canals alongside power output. Additional historical and minor structures include the Crocker-Huffman , which facilitates extractions and features a , though its operations have faced restrictions since the to protect salmonid migration. Upstream near , small diversion dams like the Cascades —used for early 20th-century water supply and minor hydro—were removed in 2004 to restore natural river processes and habitat connectivity, with no major storage reservoirs present in the upper . These facilities have enabled MID to produce an average of over 400 gigawatt-hours annually, though outputs vary with and demand.

Channelization, Flood Control, and Infrastructure

In , portions of the Merced River and its tributaries were channelized during the to mitigate flooding, stabilize banks, and protect infrastructure such as roads and buildings from erosion and high flows. These modifications involved straightening , installing revetments, and constructing channel-spanning bridges, which reduced channel roughness, promoted incision, and decoupled the river from its , limiting natural overbank flooding and deposition essential for meadow health. Following major floods, including the 1997 event that damaged facilities and highlighted vulnerabilities, the initiated restoration projects to reverse channelization effects, removing artificial constraints like excess and realigning segments to restore dynamic processes such as migration and habitat connectivity. By 2020, these efforts had focused on a 5-km reach from Happy Isles to Sentinel Bridge, emphasizing scientific design to enhance geomorphic complexity without compromising flood safety. Downstream in the Central Valley, channelization and emphasize maintenance over extensive structural alteration of the mainstem Merced River, with periodic vegetation removal and sediment clearing to sustain conveyance capacity and prevent capacity exceedance during high flows. Merced County maintains channels and levees primarily on tributaries like Black Rascal Creek, Burns Creek, and Creek, as part of the 1957 Merced County Streams Group Project integrated into the Sacramento-San Joaquin comprehensive plan, which improved downstream channels to handle waters. Limited levees exist along the Merced mainstem, where flood stages are influenced by backwater from the , prompting reliance on bypass systems like the and Eastside Bypasses for overflow diversion during extreme events. Recent experiments, such as temporary breaches on adjacent reaches, have demonstrated potential for controlled inundation to recharge and reduce peak flows, though permanent removals remain selective to balance risk. Key infrastructure includes over 10 bridges spanning the Merced in alone, such as the historic Pohono, , and Swinging bridges, which, while enabling access, have altered local hydraulics by constraining flow and exacerbating incision in some reaches. Downstream crossings, like the 1912 Shaffer Bridge (a Pratt through-truss structure) and ongoing replacements such as the Oakdale Road bridge, prioritize seismic resilience, hydraulic capacity, and roadway alignment to accommodate traffic while minimizing scour risks. Irrigation-related features diversion points and systems, exemplified by the Livingston split structure, which manages water allocation through gates and spillways to prevent and ensure efficient off-take during varying river stages.

Water Management and Rights

Allocation, Uses, and Economic Role

The Merced River's water is primarily allocated through a combination of riparian rights, pre-1914 appropriative claims, and post-1914 permits administered by the State Water Resources Control Board, with the Merced (MID) holding significant senior rights dating to its formation in 1919. MID diverts water via infrastructure including the New Exchequer (completed 1926) and McSwain (1960), storing up to approximately 1 million acre-feet combined in reservoirs for seasonal release. Annual allocations prioritize demands, with MID supplying an average of 300,000 acre-feet to irrigate about 115,000 acres across its 164,000-acre area serving over 2,200 agricultural users. Diversions occur mainly during non-winter months, but undocumented or unreported extractions by junior rights holders have contributed to critically low flows, including complete dewatering of the lower river for periods in 2014, 2015, 2016, 2021, and extensively in 2022. Primary uses of Merced River water center on agriculture, which consumes the majority via MID's canal system for crop irrigation in Merced County, supporting high-value outputs like almonds, dairy, and tomatoes. Hydropower generation from the federally licensed Merced River Hydroelectric Project (FERC No. 2179) provides secondary benefits, producing electricity sold to Central California utilities while integrating with irrigation scheduling for peak efficiency. Other allocations include municipal supply for roughly 150,000 residents, groundwater recharge to sustain aquifers, and limited industrial needs, with flood control releases managed cooperatively during high flows. Economically, the river underpins Merced 's agriculture-dependent economy, which generates billions in annual output reliant on reliable ; a 20% reduction in availability could eliminate up to $672 million in local economic activity and $167 million in labor income, per modeling by MID economists. The hydroelectric facilities contribute revenues that offset costs and support district operations, while enables farming on marginal soils, amplifying through efficient water application—Merced agriculture alone accounts for a substantial share of California's Central output, where irrigated lands produce 40% of U.S. fruits, nuts, and . Drought-induced curtailments, as in 2020–2022, have forced fallowing and crop shifts, underscoring the river's causal role in regional employment (thousands of jobs tied to irrigated farming) and GDP contributions exceeding $2 billion pre-drought impacts.

Disputes, Regulations, and Policy Debates

The Merced River's lower reaches are subject to federal protections under the Wild and Scenic Rivers Act of 1968, with approximately 71 miles designated as wild and scenic starting in 1987, primarily within and extending downstream, mandating the preservation of free-flowing conditions and outstandingly remarkable values such as scenic, recreational, and ecological attributes. These designations prohibit new dams or major diversions that impair river integrity, influencing operations at upstream facilities like the New Exchequer Dam, which provides , , and but must adhere to instream flow minima for fisheries and habitat. State regulations, enforced by the State Water Resources Control Board, include license conditions for the Merced Irrigation District (MID) requiring minimum flows—such as 100 cubic feet per second during certain periods—to support salmonid migration and riparian ecosystems, though enforcement has faced criticism for inconsistencies. Significant disputes have arisen over flow depletions, exemplified by the river running dry near Snelling in July 2023 due to MID's diversions exceeding monitored levels, prompting investigations into regulatory oversight failures and calls for permanent minimum flow mandates below Yosemite to prevent habitat desiccation for species like . In 2023, federal and state agencies, including the U.S. Fish and Wildlife Service and , intervened in litigation against MID to restore a defunct at the Crocker-Huffman Dam, arguing its absence blocks upstream passage critical for recovery under the Endangered Species Act, with courts remanding the case for trial. relicensing for the Merced River Hydroelectric Project (FERC P-2179) has involved study disputes since 2009, where environmental groups contested MID's assessments of flow impacts on downstream ecology versus generation. Policy debates center on balancing agricultural demands—MID supplies over 1 million acre-feet annually to Central Valley farms—with ecological imperatives, as evidenced by repeated congressional attempts from 2011 to 2014 by Representatives and to delist 0.6 miles of the lower Merced from wild and scenic status, enabling a 7-foot raise in Lake McClure's surface to expand storage by 12,000 acre-feet for drought resilience, opposed by conservationists as undermining the Act's free-flow prohibition. These efforts failed amid concerns over precedent for eroding protections, highlighting tensions between economic in arid regions and causal linkages between reduced flows and , with no new capacity approved but interim operating limits revised in Yosemite's 2013 Merced River Plan to sustain aquatic habitat amid visitation pressures. Ongoing management debates emphasize adaptive flow regimes to mitigate climate-driven variability, prioritizing empirical monitoring over fixed allocations to preserve geomorphic processes.

Recreation, Tourism, and Conservation

Recreational Activities and Access

The Merced River supports diverse recreational activities, including , fishing, hiking, swimming, and camping, concentrated in and adjacent public lands managed by the (BLM) and U.S. Forest Service. In , the river's calm sections from Stoneman Bridge to Bridge permit daily and inflatable when the gage height at Pohono Bridge exceeds 3.5 feet, typically from late May to early August depending on . Raft rentals, accommodating 2 to 4 people for 3-mile floats, operate mid-July to early August via concessionaires, with mandatory personal flotation devices for all participants and restrictions barring children under 50 pounds. Fishing targets rainbow trout and other species, requiring a California fishing license for those 16 and older, plus adherence to Wild and Scenic River designations limiting harvest to fish over 12 inches using artificial lures or flies only. Within Yosemite, the season runs from the last Saturday in April to November 15, with catch-and-release enforced from Happy Isles to Foresta Bridge for and a 5-fish daily limit for others. Hiking trails, such as the Merced River Trail from Railroad Flat Campground downstream, provide year-round access for anglers and day-users, though steep terrain along 140 limits some entry points. Access occurs primarily via California State Route 140, paralleling the river from El Portal to , with designated pullouts, bridges like Swinging Bridge in Wawona for South Fork entry, and the Briceburg for BLM-managed stretches below the park. rafting and thrive on undammed sections during April to June high flows, with launches at Redbud Boat Launch to Briceburg avoiding Class IV+ rapids upstream. Swimming and picnicking occur at sandy beaches like McCabe Flat Campground, subject to variable flows and park advisories against non-swimmers entering swift currents. Camping facilities, including BLM sites reachable via suspension bridges past Briceburg, support extended stays with amenities for these pursuits. Regulations emphasize safety, prohibiting tubing in hazardous areas and requiring permits for commercial outfitters.

Protected Status and Restoration Initiatives

Significant portions of the Merced River, particularly its upper reaches, are safeguarded within Yosemite National Park, established by Congress on October 1, 1890, encompassing about 71 miles of river corridor where park boundaries protect the free-flowing nature, water quality, and ecological integrity from development and incompatible uses. In 1987, Congress designated 122 miles of the Merced River—spanning from its headwaters in the Sierra Nevada through Yosemite to below Lake McClure—as a National Wild and Scenic River under Public Law 100-149, classifying upstream segments as "wild" (minimal human alteration), mid-reaches as "scenic" (some access but natural character preserved), and lower portions as "recreational" (with existing development but protected values). This designation, administered jointly by the National Park Service (NPS), U.S. Forest Service (USFS), and Bureau of Land Management (BLM)—with BLM overseeing 12 miles of rapids-focused corridor—prohibits new dams or diversions that impair outstanding scenic, recreational, geologic, fish, wildlife, historic, and cultural values, while requiring comprehensive management plans to guide land use. The NPS's Merced River Plan, finalized in September 2021 after environmental impact analysis, implements Wild and Scenic requirements by limiting user capacity in (e.g., capping campsites and lodging units to prevent overcrowding impacts on riverbanks), enforcing riparian setbacks for infrastructure, and monitoring to sustain native species like Yosemite toad and Little Kern . These measures address legacy effects from 20th-century park development, such as channelized banks and structures, prioritizing natural dynamics over engineered stability. Restoration initiatives have focused on reversing anthropogenic alterations, particularly after the January 1997 flood that scoured and exposed entrenched channels. NPS-led projects since 1998 include reconfiguring 2.5 miles of river in the Valley by removing , placing large woody debris for complexity, revegetating with native willows and sedges on 50+ acres, and to exclude and human trampling, thereby restoring meandering patterns, overbank flooding, and riparian ecosystems that support . In the lower Merced, the Merced Irrigation District's Instream and Off-Channel Restoration Project, completed in phases through 2020, rehabilitated 0.5 miles of mainstem channel and 7 acres of for and , incorporating gravel augmentation and side-channel creation to mimic pre-mining conditions altered by 19th-century hydraulic operations. Further efforts under the NOAA-supported Merced River Corridor Restoration Plan (Phase IV, initiated 2010s) target dredger sites, planning sediment removal and native planting across 100+ acres to reconnect floodplains and boost salmonid spawning success, with monitoring showing increased juvenile outmigration post-intervention. These initiatives, funded partly by federal Sport Fish Restoration Act grants, emphasize empirical geomorphic modeling and pre/post metrics like rates, rather than unsubstantiated ecological assumptions.

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