Overview

Comprehensive Description

Description

Common names: totoaba (English), totoaba (Espanol), corvinata (Espanol)
 
Totoaba macdonaldi (Gilbert, 1890)


Totoaba



Elongate, fusiform, compressed; head pointed; eye moderate size; mouth large, oblique, lower jaw a little projecting; snout with 5 pores; chin with 6 pores, no barbels; teeth in narrow bands, somewhat enlarged and conical on outer row of top jaw, including a few sharp teeth at tip of jaw; inner teeth of lower jaw slightly larger than those of outer row; 15-20 gill rakers; preopercle smooth; dorsal fin strongly notched but not divided, X + I, 23-26; anal fin short based (7-8 soft rays), 2nd  spine moderate (~ 2/3 length of 1st  ray); tail bluntly (strongly in juveniles) pointed; scales rough on head and body, smooth under head; soft dorsal and anal fins without scales; 50-56 pored lateral line scales.


Dusky silver, fins darker; juvenile spotted.


Reaches 200 cm and nearly 100 Kg.

Habitat: benthic on soft bottoms, entering rivers to spawn, juveniles usually in river mouths and around rock reefs.

Depth: 0-25 m.



Northern 2/3 of the Gulf of California.

Formerly very abundant, but now stock is seriously depleted due to overfishing. A much sought after food fish.

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Biology

Found in coastal waters; juveniles in river mouths and near rocky coasts (Ref. 9118). Feed on fishes and shrimps (Ref. 9118).
  • Chao, L.N. 1995 Sciaenidae. Corvinas, barbiches, bombaches, corvinatas, corvinetas, corvinillas, lambes, pescadillas, roncachos, verrugatos. p. 1427-1518. In W. Fischer, F. Krupp, W. Schneider, C. Sommer, K.E. Carpenter and V. Niem (eds.) Guia FAO para identificacion de especies para los fines de la pesca. Pacifico Centro-oriental. 3 volumes. 1813 p. (Ref. 9118)   http://www.fishbase.org/references/FBRefSummary.php?id=9118&speccode=13985 External link.
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Distribution

Range Description

This species is endemic to the Eastern Pacific, and is only found in the central and northern Gulf of California, Mexico. The species spawns in the northernmost part of the gulf in the Colorado River Delta. Historically, it may have also spawned farther south on the eastern side of the Gulf in large river mouths, especially the Rio Fuerte (Gilbert 1890). Sporadic young adults have been reported in sport fisheries in the southern gulf in areas of rocky reefs.
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National Distribution

United States

Origin: Exotic

Regularity: Regularly occurring

Currently: Absent

Confidence: Confident

Type of Residency: Year-round

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Global Range: Northern Sea of Cortez (Gulf of California). Leaves deep water in northern half of Gulf in spring and migrates northward in shallower waters along the east side of the Gulf to the spawning area near the mouth of the Colorado River.

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Historic Range:
Mexico (Gulf of California)

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Depth

Depth Range (m): 0 (S) - 25 (S)
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Zoogeography

See Map (including site records) of Distribution in the Tropical Eastern Pacific


 
Global Endemism: All species, East Pacific endemic, TEP non-endemic

Regional Endemism: All species, Tropical Eastern Pacific (TEP) non-endemic, Temperate Eastern Pacific, primarily, Cortez province endemic, Continent, Continent only

Residency: Resident

Climate Zone: North Temperate (Californian Province &/or Northern Gulf of California), Northern Subtropical (Cortez Province + Sinaloan Gap)

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Eastern Central Pacific: Gulf of California. Formerly abundant, now threatened by extinction due to fishing and habitat change (Ref. 27438). International trade banned (CITES I, since 4.2.1977).
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Physical Description

Morphology

Size

Length max (cm): 200.0 (S)
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Size

Length: 200 cm

Weight: 90000 grams

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Maximum size: 2000 mm TL
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Max. size

200 cm TL (male/unsexed; (Ref. 9118)); max. published weight: 100.0 kg (Ref. 32717); max. reported age: 15 years (Ref. 796)
  • Chao, L.N. 1995 Sciaenidae. Corvinas, barbiches, bombaches, corvinatas, corvinetas, corvinillas, lambes, pescadillas, roncachos, verrugatos. p. 1427-1518. In W. Fischer, F. Krupp, W. Schneider, C. Sommer, K.E. Carpenter and V. Niem (eds.) Guia FAO para identificacion de especies para los fines de la pesca. Pacifico Centro-oriental. 3 volumes. 1813 p. (Ref. 9118)   http://www.fishbase.org/references/FBRefSummary.php?id=9118&speccode=13985 External link.
  • Beverton, R.J.H. and S.J. Holt 1959 A review of the lifespans and mortality rates of fish in nature and their relation to growth and other physiological characteristics. p. 142-180. In G.E.W. Wolstenholme and M. O'Connor (eds.) CIBA Foundation colloquia on ageing: the lifespan of animals. volume 5. J & A Churchill Ltd, London. (Ref. 796)   http://www.fishbase.org/references/FBRefSummary.php?id=796&speccode=268 External link.
  • Barrera Guevara, J.C. 1990 The conservation of Totoaba macdonaldi (Gilbert), (Pisces: Sciaenidae), in the Gulf of California, Mexico. J. Fish Biol. 37 (Suppl. A):201-202. (Ref. 32717)   http://www.fishbase.org/references/FBRefSummary.php?id=32717&speccode=6317 External link.
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Type Information

Type for Cynoscion macdonaldi
Collection: Smithsonian Institution, National Museum of Natural History, Department of Vertebrate Zoology, Division of Fishes
Year Collected: 1889
Locality: Gulf of California, Mexico, Pacific
Depth (m): 37 to 37
Vessel: Albatross
  • Type:
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Ecology

Habitat

Habitat and Ecology

Habitat and Ecology
This demersal species is found in shallow coastal waters to depths of 25 m. It is one of the largest fishes in the family Sciaenidae, with a maximum reported length of almost two m and weight of 100 kg. This species has an annual spring breeding migration to the shallow, formerly brackish (now hypersaline) waters of the Colorado River delta at the extreme northern end of the Gulf. It feeds on fishes and shrimps.

The generation length for this species is estimated to be 19 years, based on an estimated average age of first reproduction of seven years and a maximum age of 30 years (Cisneros-Mata et al. 1995).

Systems
  • Freshwater
  • Marine
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Depth range based on 3 specimens in 1 taxon.
Water temperature and chemistry ranges based on 2 samples.

Environmental ranges
  Depth range (m): 4 - 37
  Temperature range (°C): 22.948 - 22.948
  Nitrate (umol/L): 2.687 - 2.687
  Salinity (PPS): 35.311 - 35.311
  Oxygen (ml/l): 4.912 - 4.912
  Phosphate (umol/l): 0.885 - 0.885
  Silicate (umol/l): 7.399 - 7.399

Graphical representation

Depth range (m): 4 - 37
 
Note: this information has not been validated. Check this *note*. Your feedback is most welcome.
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Habitat Type: Marine

Comments: Deeper waters of northern Gulf of California. Spawns in mouth of Colorado River, northern Gulf of California.

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Habitat

Salinity: Marine, Brackish, Freshwater

Inshore/Offshore: Inshore, Inshore Only

Water Column Position: Mid Water, Near Bottom, Bottom, Bottom + water column

Habitat: Reef (rock &/or coral), Reef and soft bottom, Soft bottom (mud, sand,gravel, beach, estuary & mangrove), Mud, Sand & gravel, Estuary, Water column

FishBase Habitat: Bentho-Pelagic
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Environment

benthopelagic; brackish; marine; depth range 10 - ? m
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Migration

Non-Migrant: No. All populations of this species make significant seasonal migrations.

Locally Migrant: Yes. At least some populations of this species make local extended movements (generally less than 200 km) at particular times of the year (e.g., to breeding or wintering grounds, to hibernation sites).

Locally Migrant: No. No populations of this species make annual migrations of over 200 km.

Migrates between spawning and nonspawning habitats.

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Trophic Strategy

Found in coastal waters; juveniles in river mouths and near rocky coasts. Feeds on fishes and shrimps.
  • Chao, L.N. 1995 Sciaenidae. Corvinas, barbiches, bombaches, corvinatas, corvinetas, corvinillas, lambes, pescadillas, roncachos, verrugatos. p. 1427-1518. In W. Fischer, F. Krupp, W. Schneider, C. Sommer, K.E. Carpenter and V. Niem (eds.) Guia FAO para identificacion de especies para los fines de la pesca. Pacifico Centro-oriental. 3 volumes. 1813 p. (Ref. 9118)   http://www.fishbase.org/references/FBRefSummary.php?id=9118&speccode=13985 External link.
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Feeding

Feeding Group: Carnivore

Diet: mobile benthic crustacea (shrimps/crabs), bony fishes
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Life History and Behavior

Life Expectancy

Lifespan, longevity, and ageing

Maximum longevity: 15 years (wild)
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Reproduction

Spawns in spring.

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Reproduction

Egg Type: Pelagic, Pelagic larva
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Conservation

Conservation Status

IUCN Red List Assessment


Red List Category
CR
Critically Endangered

Red List Criteria
A2bcd

Version
3.1

Year Assessed
2010

Assessor/s
Findley, L.

Reviewer/s
Carpenter, K., Polidoro, B., Livingstone, S. (Global Marine Species Assessment Team)

Contributor/s

Justification
This species is endemic to the Gulf of California. Although once considered abundant, this species' population has been decimated since the 1940s due to intensive overfishing and spawning habitat loss from conversion and degradation of the Colorado River Delta. Even though some conservation measures are in place, juveniles are still severely overfished by continued capture in shrimp trawling fisheries. Based on fisheries data available only until 1975, more than 95% decline in this species' population has been estimated over the past three generation lengths (60 years). Although some conservation measures are currently in place, there is still intensive fishing pressure and habitat degredation throughout this species very restricted range. It is listed as Critically Endangered.

History
  • 1996
    Critically Endangered
    (Baillie and Groombridge 1996)
  • 1994
    Endangered
    (Groombridge 1994)
  • 1990
    Endangered
    (IUCN 1990)
  • 1988
    Endangered
    (IUCN Conservation Monitoring Centre 1988)
  • 1986
    Endangered
    (IUCN Conservation Monitoring Centre 1986)
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National NatureServe Conservation Status

United States

Rounded National Status Rank: NNA - Not Applicable

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NatureServe Conservation Status

Rounded Global Status Rank: G1 - Critically Imperiled

Reasons: Occurs in the northern Sea of Cortez (Gulf of California), spawns near mouth of Colorado River; population reductions have been due to overfishing and reduced flow of Colorado River and consequent alteration of spawning and nursery habitat; current threat is excessive incidental take in shrimp and gillnet fisheries.

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Current Listing Status Summary

Status: Endangered
Date Listed: 05/21/1979
Lead Region: Foreign (Region 10) 
Where Listed:


Population detail:

Population location: entire
Listing status: E

For most current information and documents related to the conservation status and management of Cynoscion macdonaldi , see its USFWS Species Profile

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Conservation status

IUCN Red List: Listed, Critically endangered

CITES: Listed, Appendix I
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Population

Population
Current population status is unknown. Unpublished data and incomplete fisheries data has only been collected in the 1980s by the Federal Department of Fisheries of Mexico. However, the population of this species, once considered to be very abundant, has been severely reduced since the 1940s by overfishing.

Population Trend
Decreasing
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Threats

Threats

Major Threats
The species has been seriously depleted due to overfishing and habitat alteration. The fish formerly supported an important commercial fishing industry and sport fishery in the Gulf of California. Historically, the majority of the commercial catch was exported from Mexico to the United States, where prices were high. Overfishing of adults occurred primarily during their annual breeding migrations to the Colorado River delta. Peak annual yield in 1942 was 2,261 tonnes, and despite intensified fishing effort and increased gear efficiency, the annual yield exhibited erratic fluctuations and decreased to approximately 58 tonnes in 1975. This represents a more than 95% decline over the past 65 years (1942–2007).

Current heavy fishing pressure continues on juveniles ("machorros," 20-25 cm) due to the active shrimp trawl fishery in the upper Gulf of California. Because of historical and current overfishing, the once maximum size of 200 cm for the species has been greatly reduced.

An Environmental Assessment Study by NOAA and the U.S. Fish and Wildlife Service noted that diversion of the Colorado River has converted the formerly brackish-water habitat, in the extreme northern Gulf of California, into a hypersaline environment, drastically altering the nursery grounds of the Totoaba (Guevara 1990), and altering the life history of the species (Rowell et al. 2008).
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Critically Endangered (CR) (A2bcd)
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Comments: Population reductions have been due to overfishing and reduced flow of Colorado River and consequent alteration of spawning and nursery habitat. Current threat: excessive incidental take in shrimp and gillnet fisheries.

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Management

Conservation Actions

Conservation Actions
A total ban on fishing was declared by the Mexican Government in 1975 and this species was placed on the Mexican Endangered Species List (PROY-NOM-059-SEMARNAT-2000). In 1976, it was placed on the endangered list (Appendix I , threatened with extinction) of the Convention on International Trade in Endangered Species (CITES). In September 1978, the U.S. National Marine Fisheries Service held a workshop to evaluate the biological status of the totoaba, and in May 1979 it was added to the U.S. Endangered Species list, Federal Register 44(99): 29478-29480.

However, illegal fishing for this species in spawning grounds continued for several years after these conservation measures were enacted, and was only brought under effective control in the 1990s. The spawning grounds are in a biosphere reserve established in 1983, and the mesh size of the large gillnets formerly used for its capture have been reduced by half (from 12 inches to six inches). However, there are no data that shows whether the population is recovering. A small size cultivation effort has been in operation in Ensenada, Baja California, for the past few years and some releases into the wild have been conducted, although there is no known benefit to the population at present.
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Relevance to Humans and Ecosystems

Benefits

Importance

fisheries: commercial; gamefish: yes
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Wikipedia

Totoaba

The totoaba or totuava (Totoaba macdonaldi) is a marine fish of the drum family (Sciaenidae) that is indigenous to the northern half of the Gulf of California in Mexico. Formerly abundant and subject to an intensive fishery, the totoaba has become rare, and is listed on CITES[1], the IUCN Red List of Threatened Species[2], and the Endangered Species Act (ESA).[3]

The totoaba can grow up to two metres in length and 100 kg in weight. Their diet consists of finned fish and crustaceans. While individuals may live up to fifteen years, sexual maturity is usually not reached until the fish are six or seven years old. As totoaba spawn only once a year, population growth is slow, with a minimum population doubling time of four-and-a-half to fifteen years.[1] The totoaba spawn in the Colorado River delta, which also serves as a nursery for the young fish. The diversion of water from the Colorado River within the United States leaves little or no fresh water to reach the delta, greatly altering the environment in the delta, and the salinity of the upper Sea of Cortez. The flow of fresh water to the mouth of the Colorado since the completion of the Hoover and Glen Canyon dams has been only about 4% of the average flow during the period from 1910 to 1920. This is considered to be a major cause of the depletion of the totoaba population.[4][5][6][7]

The totoaba population is found in two distinct groups. Larval and juvenile stages occupy the Colorado delta, while the adult breeding population lives for most of the year in deeper water towards the middle of the Sea of Cortez. The adult population migrates to the Colorado delta in April and May to spawn. One-year old totoaba are metabolically most efficient in brackish water of about 20 ppt (parts per thousand) salinity, a level that occurred naturally in the delta before the diversion of water from the river that occurred in the middle of the 20th century. with the loss of the fresh water flow from the river, salinity in the delta is usually 35 ppt or higher.[7]

Commercial fishing for totoaba began in the 1920s. The catch reached 2,000 metric tons in 1943, but had fallen to only 50 tons in 1975, when Mexico protected the totoaba and banned the fishery. Anectodal evidence suggests that totoaba were very abundant prior to the start of the commercial fishery, but there is no hard evidence of natural population size. Recent studies indicate that the totoaba population has stabilized at a low level, perhaps a bit bigger than when the commercial fishery was banned in 1975. Totoaba are still caught, as by-catch in fishing for other finned fish and for shrimp, and in illegal fishing for totoaba directly. Some totoaba are illegally exported to the United States, often misidentified as white seabass.[4][5][7] The government of Baja California has authorized commercial raising of totoaba in fish farms.[8][9]

Notes

  1. ^ a b Fish Base - Totoaba - Retrieved July 11, 2007
  2. ^ IUCN Red List of Threatened Species - Totoaba macdonaldii - Retrieved July 11, 2007
  3. ^ NOAA Fisheries Office of Protected Resources - Totoaba - Retrieved July 11, 2007
  4. ^ a b Sonoran Desert Coastal Conservation - Totoaba - Retrieved July 11, 2007
  5. ^ a b Monterey Bay Aquarium Seafood Watch - Totoaba - Retrieved July 11, 2007
  6. ^ Earstones Tell Fishes' Tale in Colorado River Estuary - Retrieved June 10, 2008
  7. ^ a b c Review of CITES Appendixes Based on Resolution Conf. 9.24 (Rev.) Totoaba macdonaldi (Mexican seabass) - Retrieved July 11, 2007
  8. ^ Penuelas Alarid, Bernardo (31 October 2010). "Comercializarán totoaba criada en cautiverio". El Mexicano. http://www.el-mexicano.com.mx/informacion/noticias/1/3/estatal/2010/10/31/434856/comercializaran-totoaba-criada-en-cautiverio.aspx. Retrieved 4 September 2011. (Spanish)
  9. ^ Santos Malagón, Sac-Nicté (6 September 2010). "Buscan hacer de la totoaba un producto distintivo". La Voz de la Frontera. http://www.oem.com.mx/lavozdelafrontera/notas/n1772621.htm. Retrieved 4 September 2011. (Spanish)
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Names and Taxonomy

Taxonomy

Comments: Formerly included in the genus Cynoscion; Fuller et al. (1999) used the name Totoaba macdonaldi for this species.

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