Showing posts with label Utah. Show all posts
Showing posts with label Utah. Show all posts

Monday, 24 November 2025

Athenar bermani: A new species of Diplodocoid Sauropod from the Late Jurassic Morrison Formation of Dinosaur National Monument, Utah.

In 1913 prolific American fossil hunter Earl Douglass excavated a Sauropod braincase and partial skull roof from the Carnegie Quarry site at Dinosaur National Monument in Utah. This made its way to the collection of the Carnegie Museum in Pittsburgh, where it was given the specimen number CM 26552, and was largely forgotten for half a century (to give some context, Douglass excavated over 300 tonnes of material, including many complete skeletons of Jurassic Dinosaurs such as Diplodocus, Dryosaurus, Stegosaurus, Barosaurus, Camarasaurus, and Brontosaurus, which may have left museum staff a bit busy).

In 1978, palaeontologists David Berman and John McIntosh published a study in which they revised the genera Diplodocus and Camarasaurus, in which they assigned the specimen CM 26552 to Diplodocus. However, since that time our understanding of Sauropods as a group has developed significantly, notably in that proportional differences, which could change significantly as Sauropods grew, are no longer given the same emphasis, with modern palaeontologists instead placing more emphasis on character states (discrete features which can be present or absent).

In a paper published in the journal Palaeontologica Electronica in October 2025, John Whitlock of the Department of Science and Mathematics at Mount Aloysius College and the Section of Vertebrate Paleontology at the Carnegie Museum of Natural History, Juan Pablo Garderes and Pablo Gallina of the Consejo Nacional de Investigaciones Científicas y Técnicas, the Argentina and Fundación de Historia Natural Félix de Azara, and the Centro de Ciencias Naturales, Ambientales y Antropológicas at Universidad Maimónides, and Matthew Lamanna, also of the Section of Vertebrate Paleontology at the Carnegie Museum of Natural History, formally redescribe specimen CM 26552, assigning it to a new species and genus.

Based upon their inspection of CM 26552, Whitlock et al. conclude that it should be placed in the Dicraeosauria, a sub-group of the Diplodocidae, the skulls of which can be determined by (1) the presence of postparietal and frontoparietal fenestrae, (2) the exclusion of the basioccipital from the dorsal margin of the occipital condyle by the exoccipitals, (3) the presence of a distinct prong on the squamosal, (4) the contribution of the frontal to the margin of the supratemporal fenestra, (5) an expanded crista prootica, (6) a free dorsal margin of the antotic process, (7) the presence of a “shelf” overhanging the foramen for the trigeminal (V) nerve, and (8) the flat distal margin of the paroccipital process.

Braincase CM 26552 in anterior (A), (C) and posterior (B), (D) views. Abbreviations: BO, basioccipital; BS, basisphenoid; BT, basal tubera; CPR, crista prootica; EO-OP, exoccipitalopisthotic; F, frontal; LS, laterosphenoid; OS, orbitosphenoid; P, parietal; PO, postorbital; POP, paroccipital process; PR, prootic; S, shelf overhanging the opening for cranial nerve V; SOC, supraoccipital; SQ, squamosal; I, opening for cranial nerve I; II, opening for cranial nerve II; IV, opening for cranial nerve IV; V, opening for cranial nerve V. Whitlock et al. (2025).

Within that group, however, specimen CM 26552 shows a unique combination of features, not seen in any other genera, plus one unique character state,  the presence of a ‘tooth’ in the parietal/opisthotic suture, which has not previously been seen. For this reason, Whitlock et al. assign CM 26552 to a new species and genus, under the name Athenar bermani, where 'Athenar' honours the musician Athenar, 'for whom no better palaeontological comparison exists than a broken skull', and 'bermani' honours palaeontologist David Berman, who did so much of the fundamental modern work on Diplodocoid skulls at Carnegie Museum of Natural History and was responsible for the initial description of the specimen. 

Given the limited material available, no size estimate is made for Athenar bermani, although Whitlock et al. note that it appears to have been larger than the mature Diplodocus CM 11161, but shows incomplete fusion of many of the sutures of the braincase, suggesting that the specimen was a subadult at its time of death. 

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Saturday, 10 June 2023

Iani Smithi: A new species of Rhabdodontomorph Iguanodontian Dinosaur from the Cretaceous Cedar Mountain Formation of Utah.

The Cenomanian (Earliest Late Cretaceous) Mussentuchit Member of the Cedar Mountain Formation, which outcrops in central Utah, is one of the most abundant Late Cretaceous bonebeds known from anywhere in the world, with more than 100 species described to date, including Tyrannosaurids, Dromaeosaurs, Velociraptors, Troodontids, Therizinosaurs, Titanosauromorphs, Thescelosaurids, Pachycephalosaurids, Neoceratopsians, Nodosaurids, Hadrosaurids, and non-Hadrosaurid Iguanodontians, as well as a number of less well defined specimens.

In a paper published in the journal PLoS One on 7 June 2023, Lindsay Zanno, Terry Gates, and Haviv Avrahami of Paleontology Research at the North Carolina Museum of Natural Sciences, and the Department of Biological Sciences at North Carolina State University, Ryan Tucker of the Department of Earth Sciences at Stellenbosch University, and Peter Makovicky of the Department of Earth and Environmental Sciences at the University of Minnesota, describe a new species of Rhabdodontomorph Iguanodontian Dinosaur from the Cedar Mountain Formation.

The new species is described upon the basis of a single partial skeleton (specimen NCSM 29373) comprising a largely complete, disarticulated skull; cervical, dorsal, sacral, and caudal vertebrae; associated ribs and haemal arches; and portions of the right and left pectoral girdle, left pelvic girdle, right forelimb, and right hindlimb. The elements of the briancase are incompletely fused, leading Zanno et al. to conclude that the specimen is immature. The specimen was recovered from an exposure of the Mussentuchit Member in Emery County, Utah, 1 m above the boundary with the Ruby Ranch Member, and 7 m below Mussentuchit Ash Zones 1, which has been dated to 99.490 million years before the present. The new species is named Iani smithi, where 'Iani' refers to the Roman god Ianus (or Janus), who presides over boundaries, in reference to the fact that the mid-Cretaceous was a time of biological transition in western North America, and 'smithi' honours Joshua Aaron Smith for his contributions to the discovery and conservation of paleontological resources in the region, particularly early explorations by the North Carolina Museum of Natural Sciences.

Location of holotype locality for Iani smithi (NCSM 29373). (A) Global map showing location of Mussentuchit Member outcrop in central Utah, western North America, and a stratigraphic section at the quarry with dated ash horizons; and (B) graphical representation of preserved skeletal elements of the holotype specimen (NCSM 29373). Preserved elements are coloured on the left facing skeletal whether they derive from the right or left side of the body. Exact positions of chevrons and ribs unknown due to poor preservation. See text and figures for specific positioning and completeness of elements. Abbreviations: MAZ1–4, Mussentuchit Ash Zones 1–4. Zanno et al. (2023).

Most of the skull is present, but the missing elements include the nasal and maxilla bones, so that the length and shape of the face of Iani smithi can only be estimated from the length of the mandible. This mandible comprises fragmentary predentary, complete pair of dentaries, right surangular, partial splenial, and several isolated dentary teeth. The rear part of the premaxila is thickened and shows the alveoli (sockets) of three premaxilary teeth. Premaxilary teeth are unusual in Ornithopod Dinosaurs, with most groups having lost them early in their history, but they are known in several other Rhabdodontomorphs.

Three-dimensional reconstruction of the skull of Iani smithi (NCSM 29373). (A) right lateral and (B) medial views of skull with left facial bones removed; skull reconstruction with all preserved elements (some mirrored) in (C) caudal, (D) dorsal, (E) ventral, and (F) rostral views. Scale bar 5 cm. Zanno et al. (2023).

The dentition of Iani smithi appears similar the other Rhabdodontomorphs, and non-Rhabdodontomorph early-branching Ornithopods such as Tenontosaurus and Qantassaurus. All of the teeth on the left dentary are still present, although the crowns of the middle teeth are damaged. Five teeth are still present in the left dentary, and thirteen loose teeth were found with the skeleton, interpretted as eight maxillary teeth, five dentary teeth, and a tooth of indeterminate origin. A single predentary tooth is present.

Predentary, dentary, and surangular of Iani smithi (NCSM 29373). Predentary in (A) right lateral, (B), rostral (right half mirrored and combined to show approximate shape of complete element), (C) ventral, and (D) dorsal views. Right dentary in (E) lateral view; left (pathological) dentary in (F) medial, (G) lateral, (H) dorsal, and (I) ventral views; right surangular in (J), lateral and (K), medial views. Abbreviations: a.co, estimated coronoid articulation; ad, accessory denticle; a.pd, predentary articulation; a.sr, surangular articulation; de, dentary; dp, dorsal process; dpa, dentary parapet; f, foramen; lg, lateral groove; mkc, Meckelian canal; ml, midline; path, pathological bone; pd, primary denticle; pathological bone; pr?, prearticular?; prd, peripheral denticle; sb, surangular boss; te, teeth; tr, exposed tooth root; vp, ventral process. Colour annotation: white, depressions/fossae/grooves; green, articular surfaces; blue circles, foramina; light blue lines, marginal contours; peach dashed lines, ridges/internal contours; light purple, dentition. Scale bar 5 cm. Zanno et al. (2023).

Portions of at least seven cervical (neck) vertebrae are present, although the atlas vertebra (which connects the spine to the skull) is absent. The axis (second vertebra) is present, and is compressed dorsoventrally, somewhat eroded ventrally, and approximately 150% longer than wide. At least eight unfused neural arches from the dorsal part of the spine are preserved, along with two partially fused dorsal vertebrae are preserved in variable states of damage and distortion. The dorsal vertabrae appear to be shorter and more gracile towards the head. Six sacral neural arches and four isolated sacral centra are present, showing the sacrum to have been unfused. The first seven caudal (tail) vertebrae are also present. 

Sacral vertebrae of Iani smithi (NCSM 29373). Neural arch of S1 in (A) dorsal and (D) cranial views; (B) sacral neural arches 1–6 in left lateral view; (C) neural arch of S6 in caudal view; (E) neural arch of S2 in cranial view; (F) neural arch of S4 in cranial view; (G) neural arch of S5 in cranial view; (H) neural arch of S4 in caudal view; Sacral centrum S1? in (I) left lateral, (J) caudal, and (L) cranial views; Sacral centra S2?–5? in (K) left lateral and (N) ventral views; (M) sacral centrum S2? In cranial view; (O) sacral centrum S5? in caudal view. Abbreviations: ipodf, infrapostdiapophyseal fossae; ns, neural spine; pop, postzygapophysis; prz, prezygapophysis; vk, ventral keel. Colour annotation: white, depressions/ fossae/grooves; green, articular surfaces; blue circles, foramina; light blue lines, marginal contours; peach dashed lines, ridges/internal contours. Scale bar 5 cm. Zanno et al. (2023).

At least fourteen dorsal ribs are present, these being more robust and strongly bowed than in other Rhabdodontomorphs. Both scapulae are preserved, these being stout and robust, but within the range of other Rhabdodontomorph species. An incomplete right humerus is present, with most of the proximal portion preserved, with the exception of most of the deltopectoral crest, but the distal portion is missing. The right ulna is well preserved and undistorted. A portion of a radius is also present, though this is highly eroded and lacks both ends, making it unclear which side it came from. Four elements of a manus (hand) are present; these are poorly preserved and somewhat compressed, making identification difficult, although they may be two metacarpals and penultimate and ultimate (ungual) phalanges of digits 1, 2, or 3. Few early-branching Ornithopods have well preserved manus, making comparison between these elements difficult. The shaft and distal end of the left ischium are preserved; the shaft is generally straight, but has a twist towards the distal end. The right femur is preserved, generally in good condition, but with some erosion in the region between the greater and lesser trochanters. 

Pelvic girdle and hind limb of Iani smithi (NCSM 29373). Right ischium in (A) dorsal, (B) ventral, and (C) medial views. Right femur in (D) medial, (E) lateral, (F) proximal, and (G), distal views. Abbreviations: fh, femoral head; ft, fourth trochanter; lc, lateral condyle; mc, medial condyle; op, obturator process. Colour annotation: white, depressions/fossae/grooves; green, articular surfaces; blue circles, foramina; light blue lines, marginal contours; peach dashed lines, ridges/internal contours. Scale bar 10 cm. Zanno et al. (2023).

Zanno et al. carried out several phylogenetic analyses, using a number of different matrices, which consistantly found that Iani smithi is closely related to the Rhabdodontomorphs and the non-Rhabdodontomorph Tenontosaurus, with all analyses bar one placing Iani smithi within the Rhabdodontomorphs.

Hypothesized evolutionary relationships of Iani smithi. Strict consensus tree of the Poole Matrix using (A) maximum parsimony optimality, and (B) Bayesian inference, and strict consensus tree of the Dieudonné et al. Matrix using (C) maximum parsimony optimality, and (D) Bayesian inference. Rhabdodontomorph taxa in green. Bremer support values (left) and posterior probabilities (right) shown. Grey names reflect taxa outside the illustrated clade for a particular analysis, or in the case of Dryosauridae (an ad hoc combined Operational Taxonomic Units with variable composition using different analytical approaches). Zanno et al. (2023).

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Saturday, 11 March 2023

Skier killed by avalanche in Upper Weber Canyon, Utah.

A skier has been killed and another injured in an avalanche in Upper Weber Canyon in Summit County, Utah, at about 3.30 pm on Thursday 9 March 2023. The avalanche was triggered when a guided group of skiers, inadvertently skied onto a slope where a slab of hard-packed snow overlay a weaker layer, which gave way. The slab, which was about 400 m wide traveled about 1250 m downslope, carrying two of the skiers with it. When found both were fully buried. One of the victims was taken to a nearby hospital, where they are described as being in a stable condition, while the other had stopped breathing and could not be revived.

The scene of an avalanche in Upper Weber Canyon, Utah, which killed on skier and injured another on 9 March 2022. Utah Avalanche Center.

Avalanches are caused by the mechanical failure of snowpacks; essentially when the weight of the snow above a certain point exceeds the carrying capacity of the snow at that point to support its weight. This can happen for two reasons, because more snow falls upslope, causing the weight to rise, or because snow begins to melt downslope, causing the carrying capacity to fall. Avalanches may also be triggered by other events, such as Earthquakes or rockfalls. Contrary to what is often seen in films and on television, avalanches are not usually triggered by loud noises. Because snow forms layers, with each layer typically occurring due to a different snowfall, and having different physical properties, multiple avalanches can occur at the same spot, with the failure of a weaker layer losing to the loss of the snow above it, but other layers below left in place - to potentially fail later.

Diagrammatic representation of an avalanche, showing how layering of snow contributes to these events. Expedition Earth.

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Friday, 24 February 2023

The threats facing Great Salt Lake, Utah, and finding ways to address them.

Terminal lakes occur in semi-arid regions of continental interiors where precipitation is sufficient to allow the formation of surface waters, but not sufficient to create waterways which flow to the sea, leading to the formation of an ecosystem where wetlands are maintained by the balance between precipitation and evaporation. The largest such lake in North America is Great Salt Lake in Utah, a major driver of biodiversity and economic activity in the western United States. Great Salt Lake is estimated to generate about US$2.5 billion in economic activity each year, and to support about 9000 jobs, in fields such as mineral extraction, recreation, and Brine Shrimp harvesting. Evaporation from the lake is estimated to contribute 5-10% of the snowfall onto nearby mountains, generating a further US$1.8 billion in economic activity, and supporting a further 20 000 jobs.

Great Salt Lake provides a vital link in the 'Pacific Flyway' Bird migration route, creating a food-rich habitat used by about 10 million migratory Birds each year. About 350 species of Birds are thought to depend on Great Salt Lake and its associated wetlands, including Eared Grebes, Tundra Swans, Snowy Plovers, American Avocets, and multiple species of Ducks, Phalaropes, Owls, and Blackbirds. The widespread loss of wetlands across the western United States is has made this environment an even more vital resource for wildlife.

Great Salt Lake also provides a range of ecosystem services of direct importance to Humans, including the protection of air quality, removing water pollutants, and moderating the local climate. It is also of significant cultural importance to the people of Utah, and has inspired numerous countless scientists, pioneers, artists, writers, photographers, and recreationists. As such good stewardship of the lake is important not only because of its ecological, environmental, and economic importance, but also because of its central place in the culture of the state.

However, in recent years, the extraction of water by Humans has driven the lake far beyond the natural fluctuations that it has endured over the past millennia, pushing the lake-associated ecosystems into structural decline. Since 2020 Great Salt Lake has lost over 1.2 billion cubic metres of water per year, a trend which could see the lake disappear completely by 2028. The lake is currently 3.5 m lower and 7.4 billion cubic metres short of its minimum healthy level, and has reached this minimum on only a single occasion since 2002.

In a report published by Plant and Wildlife Services at Bingham Young University on 4 January 2024, a team of scientists headed by Benjamin Abbott of Bigham Young University, lay out the current threats faced by Great Salt Lake, and discuss the measures that could be taken to address them.

A bridge where the Bear River used to flow into Great Salt Lake. EcoFlight in Abbott et al. (2023).

The nature of saline lakes is highly dependent on the relationship between precipitation and evaporation. If there is to little rainfall or two much evaporation, then the lake becomes to saline to support the micro-organisms at the base of its food chain. Conversely, if there is to much rainfall, or to little evaporation, then the lake becomes less saline, altering the community which can live there. Water extracted from the lake or its watershed for use in agriculture can alter this balance, harming the lake's delicate ecology. Water extraction for agriculture is known to have been affecting Great Salt Lake since the mid-1800s, becoming the dominant controlling force in the watershed in the twentieth century. During this period, numerous federal and state projects, including dams, canals, and pipelines, took water from the watershed for use in agriculture, industry, and municipal purposes. This high extraction caused water levels in Great Salt Lake to fall precipitously from the 1960s, although a 'pluvial' period of high rainfall in the 1980s enabled it to recover somewhat.

Elevation, extent, and volume of Great Salt Lake from 1985 to 2022. The mean natural values were determined from estimated 1850-2016 values without Human water use. The 1985 lake level is close to the long-term natural average of 4207 foot (1313 m) above sealevel, providing a useful comparison. Abbott et al. (2023).

During the past three years Great Salt Lake has received less than a third of its natural water-input, due to excessive water extraction for Human purposes. In 2022 the lake surface dropped to its lowest ever recorded elevation, 4188 foot (1276 m) above sealevel. These figures do not include groundwater extraction or levels, making it likely that the situation in the Great Salt Lake Basin is even more severe; the loss from the lake represents about 32 billion cubic metres, but it is likely that twice as much has been loss from the basin's aquifers, which will slow the lake's recovery even if the waterflow is restored.

Ten of the 338 bird species known to feed, breed, or seek refuge at Great Salt Lake. Mary Anne Karren, Jeff Beck, Jeremy Bekker, Russell Hatch, Travis McCabe, and Chuck Castleton in Abbott et al. (2023).

The watershed for Great Salt Lake spreads across four states, and includes the Bear, Jordan, and Weber basins. Six percent of this watershed is covered by agricultural land, drawing its irrigation from the lake's water supply; 63% of this agricultural land lies in Utah, with 31% in Idaho, 5% in Wyoming, and 1% in Nevada. Another 3% of the watershed is covered by urban development, 93% of which lies in Utah.

Map of the Great Salt Lake watershed, including the most extensive land uses (agricultural and urban). Abbott et al. (2023).

Agriculture is the single largest consumer of water from the Great Salt Lake watershed, with about 75% of the water extracted going to irrigate Alfalfa and other crops, while 5-10% is lost during transport within irrigation systems. About 9% of the extracted water is consumed during mineral extraction from the lake, while another 9% is used for domestic and urban purposes, with 90% of that estimated to be spent on outdoor water use, such as watering lawns and ornamental Plants; the amount used for internal domestic purposes is negligible, as most of this is returned to the lake via wastewater treatment plants. The remaining extracted water is used in thermoelectric power generation, industry, and mining.

Evaporation ponds on the east side of the lake seen from the International Space Station. Water is taken from the lake to accelerate evaporation and extract potash fertilizer, magnesium, sulphate, table salt, and other minerals. Alexander Gerst/European Space Agency in Abbott et al. (2023).

Climate change is also affecting Great Salt Lake, with average temperatures in Utah having risen by 2°C since 1900, which is exacerbating draughts across the southwestern United States. This climate change is thought to be responsible for about 9% of the decline in water within Great Salt Lake. This trend is likely to continue for the foreseeable future, requiring Utah's Human population to plan for a drier future.

Saline lake ecosystems are being destroyed by excess water extraction for agriculture on every continent except Antarctica. This excess water extraction has been shown to trigger a sequence of ecological and economic consequences, which are almost impossible to reverse. The circumstances of this vary from site to site, but generally involve pollution of both the water and air supply, collapse of agriculture and industry, economic depression, and a breakdown of the lake and wetland ecosystems.

Even without complete loss of the lake, exposure of large areas of the former lake bed can cause problems, as this exposes sediments often laden with large amounts of pollutants, harmful minerals, and toxins. The sediments at Great Salt Lake have been shown to contain : arsenic, cadmium, mercury, nickel, chromium, lead, copper, selenium, organic contaminants, and cyanotoxins. When exposed these substances are easily picked up and distributed by the wind, as the average particle size is about 10μm. Exposure to these substances in air pollution has been linked to a number pf medical conditions, including reproductive disfunction, developmental defects, cognitive impairment, cardiovascular damage, and cancer. At a time when awareness of the problems of air pollution have risen globally, and almost all urban communities have taken steps to improve air quality, exposed lake beds can rapidly undermine improvements that took decades to achieve. Such dusts can also damage agricultural land, damaging crops and undermining soil fertility, as well as building up on top of snow packs, where their dark colour enables them to absorb thermal energy which would normally be reflected by the white snow, leading to premature melting.

Dust from drying saline lakes. (Left) Mar Chiquita, Argentina. (Upper right) Owens Lake, California. (Lower right) Dust darkens snowpack in the Rockies causing early melt.  Jeff Schmaltz, Brian Russell, and NASA in Abbott et al. (2023).

The damage to the local ecology from the loss of a saline lake is also typically severe. Changes in the water coverage and depth affect local Plant and Animal communities, and tend, in the case of salt lakes, to be accompanied by changes in the water chemistry, which can have profound impacts across wide areas. The loss of evaporative water coming from the former lake can aridify the local climate, leading to desertification, wider swings in temperature, and lower rainfall within the catchment area, leading to further aridification. This in turn profoundly affects Human populations dependent on the lake, causing industries to collapse, loss of property values, and eventually mass migration away from the area, which in turn can lead to social conflicts and a loss of social identity.

Great Salt Lake is already showing signs of developing many of these problems, and is likely to proceed further along this path without urgent action. The salinity of the lake has already begun to rise, and ,currently sits at about 19%. At this level the micro-organisms upon which the Brine Shrimps (a vital food-source for migratory Birds) depend are becoming much less productive, and the Brine Shrimps themselves are beginning to suffer metabolic problems. The lake suffered a catastrophic crash in its Brine Fly population in 2022, and the same is currently predicted to happen to the Brine Shrimp this year (2023). Several Bird species using the lake, including Wilson’s Phalaropes and Eared Grebes, are protected by federal regulations, which might lead to the enforced stopping of some economic activities on the lake if they become threatened. Even if this does not happen, the falling water levels are predicted to make mineral extraction from the lake non-viable in 2023 or 2024. At the moment the drying lake is forming salty evaporite crusts over newly exposed sediments, but if these remain exposed for long, they are likely to be a source of dust storms; dust from the lake is already reaching areas from southern Utah to Wyoming, with the majority of dust falling in the Wasatch Front area now derived from the lake. Salt-laden dust storms can lead to severe pollution levels, and are damaging to agricultural land.

A juvenile Gull feeds on Brine Flies, which depend on microbialite habitat that is being destroyed by desiccation and salination. Mary Anne Karren in Abbott et al. (2023.

The worst problems facing Great Salt Lake can be seen in the lake's North Arm, which was cut off by a railway causeway in 1959, and now receives almost no water input. This has led to salt in the water here reaching evaporation point, which in turn has killed off all the Algae in this part of the lake and causing the food web here to collapse. In addition, water circulation in the North Arm of the lake has broken down, causing pollutants to build up, giving this part of the lake the highest methylmercury levels recorded anywhere in the United States. 

Gunnison Island and the receding hypersaline water of Great Salt Lake’s North Arm. With the island connected to the mainland, predators can access the island’s colony of American White Pelicans, which is one of the largest in the world. EcoFlight in Abbott et al. (2023).

Recent changes to legislation in Utah have favoured conservation of water within natural waterways as as something to be valued in itself, allowing farmers to leave water in streams without losing water rights. In addition, the state government has significantly raised the funding available for conservation projects in 2022, and plans to do the same again in 2023. Similar changes to federal legislation has secured extra funding for the conservation of Great Salt Lake. Furthermore, many cities, towns, and districts within the Great Salt Lake basin have introduced their own water conservation projects, and many businesses and community groups are now also seeking to play an active role in the conservation of Great Salt Lake.

All of these changes are likely to have a positive impact on the lake's survival over the next few decades - as long as the lake can survive the immediate crisis, though they are probably not sufficient to avert that crisis. All of the water conservation efforts combined in 2022 is only estimated to have increased water-flow into Great Salt Lake by 123 million square metres.

Abbott et al. call for an emergency rescue plan to be put into plan for Great Salt Lake, which should be taking steps within the first half of 2023 in order to protect the lake from catastrophic changes. The lake is currently more than three metres below its minimum healthy level, a shortfall of over 7.5 billion cubic metres of water. It will require a dramatic increase in the amount of water flowing into the lake in 2023 and 2024 in order to give the lake any hope of recovery.

Abbott et al. calculate that the minimum acceptable amount of water flowing into the lake should be three billion cubic metres per year. Analysis of the past behaviour of the lake suggests that this is the point at which the water level in the lake begins to rise rather than falling. It is also roughly 1.25 billion cubic metres per year more than is currently flowing into the lake. How much water will need to be conserved each year in order to achieve this is somewhat dependent on the weather, but Abbot et al. estimate it to be between 865 million and 1.48 billion cubic metres of water per year, which would require water use within the watershed to be cut by between 30 and 50%.

A child explores rock formations on the shore of Great Salt Lake. Angie Hatch in Abbot et al. (2023).

The first instinct of planners, when faced with water scarcity, has often been to increase the supply using 'hard' engineering solutions, such as dams or pipelines. However, over the past century numerous studies have shown that this is generally the worst answer to such problems. Abbott et al. suggest that the correct way to address water shortages is to study the natural system of the water basin in question, conserve as much water as possible, and only augment the water flow with engineered solutions as a last resort.

The reasons for doing this are not purely ecological; large scale infrastructure projects such as dams are extremely expensive, and notoriously prone to both overrunning their predicted budgets and underachieving their aims, as well as often producing risks and problems which were not anticipated at the planning phase. Even when the construction phase of such projects is successful they are often unable to cope with natural changes in the hydrological cycle or variations in water demand, which can quickly make them obsolete, particularly if they are combined with overallocation of water, changes in landuse, or variations in the climate. Notably, moving water from one area to augment the supply in another can lead the area from which water is extracted facing shortfalls of its own. 

A family enjoys the buoyancy of Great Salt Lake’s saline water. Kevin Hehl in Abbott et al. (2023).

The Great Salt Lake watershed is littered with such hard engineered water projects, including three huge pumping stations and a system of reservoirs which is calculated to lose as much water each year as the total domestic consumption within the watershed. An inter-basin transfer system also exists, which has been linked to the decline of the Colorado River water-system. However, many other proposed engineering solutions to the watershed's problems have been rejected, which Abbott et al. suggest indicates a degree of wisdom on the part of environmental managers.

Abbott et al. believe that decreasing water demand is always a better solution than trying to maintain water supplies through engineered solutions, both because it costs considerably less, and because it provides more resilience to changes in the water cycle. Careful pricing of water and caps on its usage can deliver reductions in water consumption quite quickly, and with relatively little expense. Estimates of the costs that would be associated with restoring the Great Salt Lake through water conservation alone vary between US$14 and US$96 million, or between US$5 and US$32 for every person living in the watershed, while the use of a water market system, which would give inhabitants the right to buy and sell water, could lower the cost to between US$6 and US$48 million, or between US$2 and US$14 per person living in the watershed. 

More heavily modified water-systems tend to require more maintenance than more natural, less modified systems. This is currently the case with Great Salt Lake, where almost every aspect of the ecosystem, water-flow regime, and even lake chemistry is currently controlled by Humans, While all of these controls were put in place with good intent, collectively they are responsible for the majority of the problems facing the lake today.

Abbott et al. note that returning the lake to a 'pristine', pre-Human intervention state would be neither possible nor desirable, but do believe the natural state of the lake should be a major consideration when planning future changes. Such an approach should reduce the risk of harmful side-effects occurring when well-intentioned projects are put into place, increasing the likelihood of such projects are undertaken. Particular attention should be paid to maintaining the amount of water flowing into the lake, and also the seasonal nature of such water flow, as well as to the establishing a conservation buffer zone around the lake, where natural ecosystem-processes are allowed to take precedence over infrastructure projects. Efforts should be made to keep the lakes level above its natural lowest level (1282 m above sealevel). Abbott et al. believe that restoring a more natural hydrology to Great Salt Lake will have a knock-on effect, helping to restore more natural systems to upstream environments such as Utah Lake, Jordan River, Weber River, Logan River, and Farmington Bay.

Complex dikes and flow control structures in the wetlands around the lake. EcoFlight in Abbot et al. (2023).

Environmental concerns and the maintenance of natural water systems have traditionally been given a low legal priority in western cultures. This has failed to take into account that Humans often need these natural ecosystems in order to survive and flourish. Changing the allocation of water usage between different consumer groups can deal with short term problems, but fails to address the underlying problems of water supply. Abbot et al. believe that in order for Utah to establish a maintain a sound ecological foundation upon which its Human prosperity can be based, Great Salt Lake itself must be permanently allocated a large portion of the water flowing into its watershed. Current law in the state relies on the principle that users who can establish that they have been utilizing water for longer have precedence over other users, something which Abbott et al. believe should be extended to the lake itself as an entity. If the lake is accorded such status, then a the water required to maintain the natural system would be allocated ahead of that required by Human users, thereby insuring the continuance of the lake and associated water systems.

This would mean reducing the amount of water available for Human users, but would introduce a degree of security into the system, which would be of benefit to the Human occupants of the watershed. Once the lake's needs were met any excess water could then be distributed via a system of prior application (earliest Human users first), or divided equally among users. The later system has been deployed successfully in Nevada, while the former aligns more closely with standing law in Utah. 

Abbott et al. also note that in strongly religious Utah, recognizing the Great Salt Lake as part of God's creation entrusted to Human stewardship, which therefore should have a right to continue to exist, is not at odds with the customs or beliefs of much of the population.

Great Salt Lake and its watershed seen from the International Space Station. Alexander Gerst in Abbott et al. (2023).

Abbott et al. recommend that the federal government makes more funds available for water conservation in the Great Salt Lake watershed, and takes an active role in coordinating water usage agreements across state lines. They further recommend that the federal government increases monitoring of the hydrology and climate of the basin, and that federal agencies work closely with state agencies on the monitoring and maintenance of the basin's ecosystems.

Livestock and water Infrastructure in the Heber Valley. Ben Abbott in Abbott et al. (2023).

Abbot et al. further recommend that the state authorities in Utah release water held in reservoirs in order to increase the streamflow into Great Salt Lake during 2023 and 2024, if necessarily leasing, purchasing or using emergency mandate powers to obtain water from wholesalers (although they do stress that private organizations holding water should be compensated for such seizures). They further recommend that the state establish a long-term target lake-level, using the framework suggested in previous state reports, with a well-defined, and legally binding, timeline for reaching key goals in the restoration of the ecosystem. Furthermore, they recommend that the state develops a high-profile website dedicated to promoting the wellbeing of the lake, which highlights individuals and organizations doing the most to help conserve water, and also directly contacts all water users in the watershed, as well as community, church, and agricultural groups to ensure that they are kept up to date on the progress of the program, why it is being undertaken, and any changes to the legal structure through which water allocation is handled and how it will affect users.

A Tundra Swan looks for water at the former shoreline of Great Salt Lake. Mary Anne Karren in Abbott et al. (2023).

Furthermore, Abbott et al. recommend that the state authorities should offer farmers in the watershed compensation for not growing crops this year, and provide aid to help them transition to less water-intensive crops. The state should also seek to extend develop water markets across the entire watershed, using models previously developed for the management of saline lake watersheds. The state should work with the Utah Water Task Force and other organizations to establish a 'law of the lake' framework within each of the major watershed basins, following the pattern used in the early 2000s to resolve water conflicts in the Bear River Basin. The state should be responsible for ensuring any water saved by state and federal programs is permanently assigned for the benefit of the lake, expand turf-removal programs to encourage less water-consumptive gardening practices in urban and country communities, hire more employees to work on all of these projects, and implement a system of tiered water pricing, as well as removing subsidies for water use.

An American Avocet forages for food among desiccated microbialites. Mary Anne Karren in Abbott et al. (2023).

Abbott et al. also recommend that local authorities within the Great Salt Lake watershed should coordinate with both state and federal programs to raise awareness of the problems facing the lake and its watershed, and to promote water conservation by cities, businesses, and individuals. In particular local authorities should convene homeowner and home-builder associations, who should be kept briefed on any changes to the rules regarding water management, and encouraged to take an active role in water conservation. Local authorities should also work with community groups to remove turf from public spaces, and promote less water-intensive forms of gardening, including the planting of vegetation native to the region, as well as introducing tiered charging for different water uses (in particular lower charges for indoor water use than outdoor).

Boaters, birders, and hunters access the lake’s wetlands and shallow bays. Chandler Rosenberg in Abbott et al. (2023).

Abbott et al. also make a number of recommendations for individuals and community groups within the Great Salt Lake watershed, including actively spreading information about the crisis facing the lake and the efforts being made to tackle it, sharing information about water conservation techniques, changing the vegetation in gardens and other outdoor spaces to types which need little or no irrigation, encouraging local, state, and federal authorities to adopt conservation measures, and maintaining or removing sprinkler systems.

An Eared Grebe looks to us for leadership. Mary Anne Karren in Abbott et al. (2023).

As well as a list of recommendations for things that should be done, Abbot et al. strongly advise that a number of actions be avoided. The first of these is not attempting to prevent natural evaporation from the lake (something which is often done with reservoirs) as this will effect precipitation in areas downwind of the site, and impact the natural water/mineral balance of the lake. Secondly, Abbot et al. advice against cloud seeding to try to resolve water shortage problems, noting that this is (at best) an unreliable technology, and again has the potential to upset rainfall patterns in neighbouring areas. Thirdly, Abbot et al. recommend against the building of more infrastructure, observing that reservoirs and piping systems are major causes of the current problem, and that building more it unlikely to solve the situation. Fourthly, Abbott et al. strongly advise against simply waiting for rain, noting that, while this did work briefly in the 1980s when a short pluvial interval restored much of the water to an already drying lake system, that was regarded at the time as a once-in-a-thousand-years event, and that since then a warming global climate has shifted conditions in the Great Salt Lake watershed, making a repeat of the event even less likely. Finally, Abbott et al. advise strongly against simply abandoning the lake or any part thereof (something they refer to as the Aral Sea solution). Recent speculation has been made about the possibility of abandoning the North Arm of Great Salt Lake, which was cut off by the building of a railway causeway in 1959, and now naturally receives little natural irrigation, in order to conserve water for the rest of the lake. However, this course of action would mean allowing the Pelican colony on Gunnison Island to go extinct, sacrificing a valuable mineral extraction industry on this arm of the lake, and risking the creation of a major source of toxic dusts, including methyl mercury.

Sunset over an exposed microbialite reef. Mary Anne Karren in Abbott et al. (2023).

Finally, Abbott et al. suggest that what has ultimately been missing from the Great Salt Lake watershed has been not water but trust. Water conservation measures are present throughout the watershed, but the various users have not trusted each other enough to allow conserved water back into the lake. Abbott et al. concede that the proposed changes will have the most impact on farmers and rural communities within the Great Salt Lake watershed, but stress that the majority of the authors of the report come from such backgrounds, and that they are keen to see proper support, financial, legal, and technical, for farming communities during any change within the watershed.

A woman gazes across the lake. Jared Tamez in Abbott et al. (2023).

The Great Salt Lake ecosystem is currently facing an unprecedented ecological collapse, and addressing this will require equally unprecedented changes in the way water conservation is managed within the Great Salt Lake watershed. However, Abbot et al. suggest that bold, collective action is not unprecedented in the history of Utah, and that they believe the people of the state are capable of rising to face the challenge before them. 

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