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FAO Fisheries Synopsis No.101FRm/S101
SAST - Shrimp

SYNOPSIS OF BIOLOGICAL DATA ON THE WHITE SHRIMP
Penaeus setiferus (Linnaeus) 1767

Exposé synoptique sur la biologie de
Penaeus setiferus (Linnaeus) 1767

Sinopsis sobre la biología del
Penaeus setiferus (Linnaeus) 1767

prepared by

MILTON J. LINDNER and HARRY L. COOK
Bureau of Commercial Fisheries
Biological Laboratory
Galveston, Texas 77550, U.S.A.

Contribution No.240, Bureau of Commercial Fisheries Biological Laboratory, Galveston,
Texas 77550, U.S.A.

1 IDENTITY

1.1 Nomenclature

1.11 Valid name

Penaeus setiferus (Linneaus) 1767, Syst. Nat.(ed.12) 1:1054

The controversy over the use of the name setiferus for the present species or for P. schmitti has been definitely decided in favor of the first alternative by the International Commission on Zoological Nomenclature in their Opinion 817 (1967, Bull. zool. Nomenol. 24(3):151).

1.12 Objective synonymy 1

Astacus fluviatilis, Americanus, Seba, 1759

Cancer setiferus Linnaeus, 1767

Astacus setiferus (Linnaeus) Olivier 1791

Cancer (Gammarellus) setiferus (Linnaeus) Herbst, 1793

Penaeus fluviatilis Say, 1818 (an objective synonym of Cancer setiferus L., 1767, through the type selection by Holthuis, 1964, Bull. zool. Nomencl., 21(3):233).

Penaeus setifer (Linnaeus) L. Agassiz, 1849

1 The authors wish to express their appreciation to Dr. Holthuis who provided the information in this section.

1.2 Taxonomy

1.21 Affinities

Suprageneric (to family after Waterman and Chace, 1960)

Phylum Arthropoda
  Class Crustacea
   Subclass Malacostraca
    Series Eumalacostraca
    Superorder Eucarida
     Order Decapoda
      Suborder Natantia
       Section Penaeidea
        Family Penaeidae
         Subfamily Penaeinae

Generic

Genus Penaeus Fabricius, 1798, Suppl. Ent.Syst.: 385,408. Type species, by selection by Latreille, 1810, Consid.gén.Anim.Crust. Arachn.Ins.:102,422: Penaeus monodon Fabricius, 1798, Suppl.Ent.Syst.:408. Gender: masculine.

Definition

Rostrum toothed dorsally and ventrally. Carapace without longitudinal or transverse sutures; cervical and orbito-antennal sulci and antennal carinae always present. Hepatic and antennal spines pronounces, pterygostomial angle rounded. Telson with deep median sulcus, without fixed subapical spines, with or without lateral movable spines. First antennular segment without a spine on ventral distomedian border. Antennular flagella shorter than carapace. Maxillulary palp with 2 or 3 segments, usually 3. Basial spines on 1st and 2nd pereiopods; exopods on 1st 4 pereiopods, usually present on 5th. Petasma symmetrical, pod-like with thin median lobes with or without distal protuberances; lateral lobes often with thickened ventral margin. Appendix masculina with distal segment subtriangular or avoid, bearing numerous spines. Thelycum usually with an anterior process, variable in shape, lying between the coxae of 4th pereiopods; with or without lateral plates on sternite XIV. Pleurobranchiae on somites IX to XIV: a rudimentary arthrobranch on somite VII, and a posterior arthrobranch on somite XIII; mastigobranchiae on somites VII to XII. Zygocardiac ossicle consisting of a principal tooth followed by a longitudinal row of smaller teeth which often end in a cluster of minute teeth. Body glabrous. (After Dall, 1957, slightly modified by Pérez-Farfante).

Specific

Identity of type specimens

The specimen figured by Seba (1759, Locuplet. Rer.nat.Thes. 3: pl. 17 fig. 2) is the holotype, or if the original description was based on more material, the lectotype of Cancer setiferus L. (by the selection by Holthuis, 1962, Gulf Research Rep. 1(3):115). The original type material is lost and a neotype has been designated by Burkenroad (1939, Bull. Bingham oceanogr. Coll. 6(6):17). The neotype is a male from Matanzas Inlet, Florida (0–10 fathoms, otter-trawl 2 April 1934, M.B. Bishop) in the Bingham Oceanographic Collection of Yale University, New Haven, Conn. U.S.A., preserved under no. B.O.C. 237. This neotype selection has been validated by the International Commission on Zoological Nomenclature in their Opinion 817 (1967, Bull.zool.Nomencl. 24(3):151).

Type locality

“In Indiis” (Linnaeus, 1767), restricted to “America” (Seba, 1759) by the lectotype selection (Holthuis, 1962) and still further restricted to Matanzas Inlet, Florida, U.S.A. by the neotype selection (Burkenroad, 1939).

Diagnosis

Adrostral carina not reaching behind middle of carapace; gastrofrontal carina absent; hepatic carina present; rostral teeth usually 9 dorsal, 2 ventral; anterior portion of the ventral margin of the pleuron on the 1st pleonic somite almost straight; thelycum of female with open seminal recepticle; posterior portion of 14th sternite of female with conspicuous pair of fleshy protuberances; distoventral lobule of distomedian lobe of petasma rounded and not projecting; petasma of male with diagonal ridge across ventral face of distoventral lobe (Burkenroad, 1934, 1936; Ewald, 1965).

Subjective synonymy

Penaeus orbignyanus Latreille, 1817
(see Burkenroad, 1939, p.19).

Penaeus gracilirostris Thallwitz, 1891
(see Burkenroad, 1939, p.17).

Key to species

For key to species of the western Atlantic see section 1.21 of synopsis on Penaeus schmitti by Isabel Pérez-Farfante (1970).

1.22 Taxonomic status

Penaeus setiferus is one of the about 28 species of the genus Penaeus, and the first to ever get a valid scientific name. It is very close to Penaeus schmitti Burkenroad (see Species Synopsis 10) and was only distinguished from that species as late as 1936.

1.23 Subspecies

No subspecies are currently recognized in this species.

1.24 Standard common names

U.S.A.:  white shrimp
Mexico: camarón blanco

Vernacular names

U.S.A.: common shrimp, archaic
green shrimp (Southport, N.Carolina)
     "        "       (Jacksonville, Florida)
gray shrimp (N.Carolina and Florida)
green-tailed shrimp (Pamlico Sound, N.Carolina)
blue-tailed shrimp (Ocracoke, N.Carolina)
lake shrimp (Louisiana)

1.3 Morphology

1.31 External morphology

Young (1959) described in detail the skeletal and muscle systems and discussed the nervous, circulatory, digestive, excretory, and reproductive systems. Burkenroad (1934, 1939), Rioja (1939, 1940, 1941), and King (1948) described minute details of the external and internal reproductive systems.

Williams (1965, p.18) described the color “Body translucent, bluish white with dusky bands and patches composed of scattered black specks; rostrum and sides tinged with pink; blades of pleopods marked with dark red; antennae dark brown; uropods with tips of blades dark brownish purple with narrow stripe of yellowish green along margin.”

Burkenroad (1934) reported that specimens from the Atlantic coast of the United States have longer rostrums than those from the Gulf of Mexico, but Lindner and Anderson (1956) believed Burkenroad was comparing immature Atlantic specimens with mature Gulf shrimp. Pérez-Farfante (personal communication) detected no differences between the Atlantic and Gulf of Mexico populations.

Mature shrimp have a shorter rostrum than immature shrimp of the same total length. Lindner and Anderson (1956, Fig.30) showed the relation between rostral length and total length for immature and mature female shrimp from Louisiana.

The bodies of older shrimp tend to thicken, and their weights are greater in proportion to length than are those of younger shrimp (Anderson and Lindner, 1958; Vioca, 1920).

(See also 3.11)

1.33 Protein specificity

Serological comparisons of saline-hemocyanin filtrates of P. setiferus, P. aztecus and P. duorarum from North Carolina by Leone and Pryor (1952, p.31) “… place P. aztecus and P. duorarum closer to each other than either is to P. setiferus …” and “P. setiferus is more similar to P. duorarum than it is to P. aztacus.” These authors also stated, “The serological differences are significant, and support the theory that these organisms are three distinct, but closely related, species”.

2. DISTRIBUTION

2.1 Total area

According to Pérez-Farfante (personal communication), P. setiferus is limited to the east coast of the United States and the Gulf of Mexico, land areas 235, 237, 238 and 311 of FAO distribution code (Holthuis and Rosa, 1965). It has been reported from Fire Island, New York (Burkenroad, 1939), south to St. Lucie Inlet, Florida (Gunter, 1963), with the center of abundance off Georgia and north-eastern Florida. It was generally thought to be absent between St. Lucie Inlet and Ochlocknee River, Florida (Joyce and Eldred, 1966), but Springer and Bullis (1952), recorded one specimen from about 46 m of water at lat, 24°46' N, and long. 82°59' W. From Apalachicola Bay, Florida, a concentration extending westerly and southerly to northeastern Mexico has a center of abundance in Louisiana. A third concentration in the southern part of the Gulf of Campeche extends northeasterly along the coast from about Tupilco, Tabasco to Campeche, Campeche (Lindner, unpublished records). Bullis and Thompson (1965) caught P. setiferus at lat.20°17' N, long. 91°35' W, which appears to be near the limit of its occurrence in this area. The greatest depth recorded for P. setiferus is about 82 m in the Gulf of Mexico near the mouth of the Mississippi River (Bullis and Thompson, 1965, OREGON station 1495, lat, 28°48' N, long. 89°26' W; 45 fm (82 m)).

The species is most abundant in areas characterized by extensive inland, brackish marshes connected by passes to shallow, offshore areas of relatively high salinity and mud or clay bottoms (Anderson, King and Lindner, 1949). In the bays and shallow waters along the coasts of Georgia and the northwestern Gulf of Mexico, it is most frequently taken by otter trawls in association with fishes of the Family Sciaenidae (Anderson, personal communication; Gunter, 1945).

2.2 Differential distribution

2.21 Spawn, larvae, and juveniles

Most, and possibly all, spawning of P. setiferus is at sea. Off Louisiana, spawning probably does not occur in depths less than about 9 m (Pearson, 1939; Lindner and Anderson, 1956). At Port Aransas, Texas, Heegaard (1953, p. 78) believe it “spawns immediately outside the coast at a distance of 5 to 6 miles (9.3 to 11.1 km) from shore.” Some spawning along a portion of the Atlantic coast may occur near shore. Pearson (1939) collected eggs on 5 occasions at St. Augustine Inlet, Florida, and Lindner and Anderson (1956, p. 616) on the basis of ripe shrimp taken in trawls stated, “… most spawning in Georgia and northern Florida is in outside waters more than 1 mile (1.9 km) from shore, although some spawning may actually occur in inside waters in this area.”

Off Lousiana, most spawning was in depths between 9 and 31 m (Lindner and Anderson, 1956). The greatest depth at which Pearson (1939) encountered larvae was about 55 m.

The eggs are demersal and the larval stages planktonic. Occasionally, eggs and larvae are carried into the estuaries (Pearson, 1939), but normally the young shrimp enter the estuarine nurseries as postlarvae at a total length (tip of rostrum to tip of telson) of 6 to 7 mm (Weymouth, Lindner and Anderson, 1933; Pearson, 1939; Anderson, King and Lindner, 1949; Bearden, 1961; Baxter and Renfro, 1966). On reaching the estuaries, the postlarvae become benthic (Anderson, Lindner and King, 1949; Williams, 1955). Habitats are characterized by shallow water, muddy or peaty bottoms high in organic detritus, abundance marsh grasses, moderate to low salinities, and widely fluctuating temperatures (Weymouth, Lindner and Anderson, 1933; Anderson, King and Lindner, 1949; Williams, 1955, 1955a; Loesch, 1965; Mock, MS).

As the shrimp grow, they move gradually from the shallow marginal areas to the deeper parts of the estuaries and then out to the open sea. They first appear on the estuarine fishing grounds in June or July, depending on locality, at a modal size of between 80 and 100 mm total length. Minimum length is about 50 mm (Weymouth, Lindner and Anderson, 1933; Gunter, 1950; Lindner and Anderson, 1956). Usually within a month of their appearance on the estuarine fishing grounds, some of the young have reached the open sea at a modal length of between 100 and 120 mm. This seaward movement continues throughout summer and is heightened in fall and winter by lowering temperatures (Lindner and Anderson, 1956).

2.22 Adults

See sections 2.1, 3.51, and 5.31.

2.3 Determinants of distribution changes

The determinants of distribution changes are largely unknown. Generally, it is presumed that postlarvae enter estuaries for food and shelter. Lindner and Anderson (1956) speculated that the movement from estuarine areas to the open sea was associated with approaching maturity. They and Gunter (1950) agree that this movement is intensified by falling temperatures during the latter part of the year.

Migrations along the Atlantic coast and offshore-onshore movements in the northern Gulf of Mexico during fall and winter were attributed to temperature changes by Lindner and Anderson (1956).

3 BIONOMICS AND LIFE HISTORY

3.1 Reproduction

3.11 Sexuality

Heterosexual. Sexes are easily distinguished: male with endopod of the 1st pair of pleopods modified to form a copulatory organ, the petasma; female with open type thelycum situated between the 3rd, 4th and 5th pereiopods.

Rioja (1939, 1940) described the internal or medial antennular flagellum of adult males as being thicker and more robust than that of adult females; and having 16 of its segments each bearing 1 uniformly-large central and 2 small lateral spines. The lateral spines are lacking on some of the segments however, especially on the distal ones. The spines are absent in females, which have a tuft of bristles near the base of the external border much longer than in males. Rioja (1939) believed this antennular organ of the males to be sensorial and intimately related with sexual functions.

Four male white shrimp (143 to 180 mm total length) from the Texas coast that were examined by us differed from Rioja's description, which presumably was based on shrimp from the Gulf of Campeche. Three of the shrimp had 26 of their antennular segments bearing a large central spine, and the 4th had 24. There was only 1 lateral spine per segment and not all segments with large central spines had lateral spines. The number varied from 12 to 17. Dall (1957) said in his description of the genus Penaeus that the 3rd maxilliped is sexually dimorphic. Rioja (1948) who studied in detail the 3rd maxilliped of P. californiensis Holmes, P. stylirostris Stimpson, P. vannamei Boone, and P. setiferus, stated that the 3rd maxilliped of P. californiensis was sexually dimorphic. He did not describe, however, sexual dimorphism in the other species. From this statement we conclude that Rioja found no difference between the 3rd maxilliped of P. setiferus males and females. We examined 2 females (150 and 191 mm total length) and 1 male (163 mm) from the northwestern Gulf of Mexico and could find no sex-linked differences between proportions of each segment of the 3rd maxilliped against dactylus or between the total length of the shrimp against length of 3rd maxilliped. In all 3 specimens, the 3rd maxilliped extended to the distolateral edge of the antennular peduncle.

Weymouth, Lindner and Anderson (1933) noted a difference which increased with age in mean total lengths of the sexes. This disparity was later studied by Williams (1955) who concluded that after the mean size of the shrimp in the population exceeded 100 mm, the mean total lengths of the females were consistently larger than those of the males.

3.12 Maturity

Broad (1965), intepreting length-frequency plots of Louisiana white shrimp published by Lindner and Anderson (1956), determined that sexual maturity is reached at a total length of 140 mm. Burkenroad (1934) reported that females become sexually mature at a carapace length of about 35 mm (about 165 mm total length) and that ripe sperm first appear at 25 mm carapace length (about 119 mm total length).

Distinctive changes in color and size accompany maturation of the ovary (King, 1948). Using these changes, King differentiated the following phases of development which are easily identified in the field.

Undeveloped: ovary small and transparent.

Developing: ovary opaque; scattered melanophores over the surface.

Yellow: ovary yellow to yellow-orange.

Ripe: ovary drab, olive-brown colored; very distended.

Recently spent: ovary collapsed and not as deeply colored as when ripe.

3.13 Mating

There is no record that mating has been observed, but it is believed that P. setiferus is promiscuous. The male attaches a spermatophore to the female before spawning. The spermatophore is placed externally between the 3rd, 4th, and 5th pairs of pereiopods (King, 1948).

3.14 Fertilization

Generally believed to be external; upon emission, the eggs are fertilized by sperm from the spermatophore. Cook, however, (unpublished records) reported that recently captured gravid females, without external spermatophores, spawned viable eggs in the laboratory. These eggs hatched into apparently normal larvae which were reared to subadult size. The sex ratio of the juveniles was 1:1.

3.15 Gonads

No detailed investigations have been made on the relation of gonad size and number of eggs to body length, weight, or age. It has been estimated, however, that from 500,000 to 1,000,000 eggs are produced by one individual st a spawning. Anderson, King and Lindner (1949) counted about 860,000 eggs in the ovaries of a ripe female 172 mm total length. Burkenroad (1934) reported that the spermatophores of large mature males were no larger than those from smaller mature males. King (1948), who examined the entire gonads of several specimens of both sexes, reported them to be homogenous in structure and stage of development of the germ cells.

3.16 Spawning

The number of times a white shrimp spawns in a single year is unknown. Most shrimp biologists agree that these shrimp may spawn repeatedly in a single season. Lindner and Anderson (1956) speculated that a single shrimp could spawn as many as 4 times in a season and indicated that a few females probably survived to spawn during a second season.

Weymouth et al. (1933, p. 24) stated that, “P. setiferus spawns from March or April to August or September.…” With considerably more data than those available to Weymouth et al., Lindner and Anderson (1956, p.616) concluded, “When we consider sampling technique and errors, it appears probable that there is little, if any, difference between spawning seasons in any of the localities we covered between South Carolina and Texas. There probably is not more than about 2 weeks' difference in the beginning of spawning between any of the localities. Spawning may start later in South Carolina and Georgia than it does in Florida, Louisiana, and Texas, but in all the localities it probably begins either during the latter part of March or early in April and may possibly continue on into November, though probably it is completed by the end of September.”

Lindner and Anderson (1956) placed the peak of spawning in June or July. More recent studies on ovarian development in the north-western Gulf of Mexico by Renfro and Brusher (MS) and on occurrence of larvae in plankton collections by Temple and Fischer (1968) substantiate the findings of Lindner and Anderson (1956).

Spawning in laboratory aquariums has occurred only at night. On 2 occasions, P. setiferus spawned between 2230 and 2300 Central Standard Time (Cook, unpublished records).

Spawning is associated with size and probably also with age because the largest females spawn first (Weymouth et al., 1933; Lindner and Anderson, 1956).

Spawning also appears to be affected by temperature. Lindner and Anderson (1956, p. 620) stated, “Spawning in Louisiana appears to be more closely associated with rising and falling temperatures than with absolute temperature… The comparatively abrupt rise in the spring temperature coincides rather closely with the beginning of the spawning season and may, indeed, initiate it, while the season seems to terminate as soon as the temperatures begin to decline rapidly in the fall, even though they are at that time appreciably higher than those which evidently induced spawning in the spring.”

Data from studies in areas where the 3 species P. setiferus, P. duorarum and P. aztecus occur together suggest that spawning seasons of the first 2 probably coincide. That of P. aztecus overlaps the others but its peak of spawning activity is either later or earlier (Williams, 1955; Joyce, 1965; Christmas, Gunter and Musgrave, 1966; Renfro and Brusher, MS). Temple and Fischer (1968) indicated that in the northwestern Gulf of Mexico peak spawning of P. aztecus occurs later than that of P. setiferus and that the larvae or postlarvae, or both, of P. aztecus overwinter in waters of the continental shelf.

The eggs are spawned directly into the water and there is no nesting or reproductive isolation.

Spawning activity within a season appears to increase to a single peak and then decline, but the young produced do not follow this pattern. Depending upon the locality, two or three broods of young shrimp may appear on the fishing grounds each season (Gunter, 1950; Lindner and Anderson, 1956).

3.17 Spawn

The eggs are demersal, nonadhesive and spherical. Live eggs measure 0.28 mm. Each egg has a thin, transparent membrane, or chorion, that gives a purplish-blue coloration in reflected light under the microscope (Pearson, 1939).

3.2 Pre-adult phase

3.21 Embryonic phase

In late developmental stages, the embryo is well-differentiated almost filling the egg, and leaving only a narrow perivitalline space. The length of the embryo is about 0.26 mm. The dark brown embryo is invested by a thin, transparent, and colorless embryonic membrans. Three pairs of appendages, corresponding to the 1st and 2nd antennae and mandibles, can be seen folded closely to the body. Several hours before hatching the embryo makes convulsive movements within the egg. The embryonic membrane is broken by the antennae. The egg membrane is normally ruptured soon after and the larva emerges. Actual emergence from the egg takes only a few seconds (Pearson, 1939).

3.22 Larval phase

White shrimp larvae were described by Pearson (1939) from specimens taken from the plankton. He encountered 5 nauplial substages, 3 protozoeal substages, and 2 mysis substages. Heegaard (1953) also reported 2 mysis substages but an editorial footnote suggests more than 2. Three mysis substages are present in laboratory-reared larvae (Cook, unpublished records). It is probable that Pearson did not encounter the 2nd mysis sub-stage.

Johnson and Fielding (1956) reported that the length of larval life was 10 to 12 days. They said, however, that the metamorphic period is not of fixed duration, but depends to some extent on local food and habitat. When reared in the laboratory at 30°C, larvae grew to 1st postlarvae in 9 to 13 days; those reared at 22°C required 15 to 24 days (Cook, unpublished records).

Nauplii do not feed, but utilize yolk granules which fill their body, Feeding starts at the 1st protozeal substage. In the laboratory, they are fed successfully with microscopic green algae and brine shrimp nauplii. First protozea feed while swimming; movements of the maxillae and maxillipeds produce a feeding current (Pearson, 1939).

The sizes of the various larval stages are given in Table I.

3.23 Adolescent phase

During the early postlarval stages, the young shrimp are still planktonic in the offshore waters. At a total length of about 7 mm they enter the estuarine nursery grounds and take up a benthic existence, undergoing no striking morphological changes as they continue development. Williams (1953, 1959) has given characters which allow separation of certain size ranges of postlarval white shrimp from postlarval P. aztecus and P. duorarum of comparable size.

Various estimates have been made of growth during the adolescent phase. Viosca (1920) and Gunter (1950) estimated growth at about 1.0 mm per day; Williams (1955) at 1.2 mm per day; and Lindner and Anderson (1956) at 80 mm in 2 mo or 1.3 mm per day. Loesch (1965) suggested that “very young white shrimp may grow as much as 65 mm per month” or about 2.2 mm per day. Johnson and Fielding (1956) estimated that captive postlarvae grew at a rate of 2.1 mm per day for 24 days and 1.7 mm per day for the next 28 days. R. S. Wheeler (personal communication) grew postlarvae from 12.2 mm to 92.9 mm in 5 wk during the summer in a pond at Galveston, Texas; growth rate was 2.3 mm per day.

TABLE I

Size of egg, larvae and first postlarvae of white shrimp (Pearson, 1939)

Stage of developmentLength (mm)
 Egg0.28
Nauplius I0.30–0.34
Nauplius II0.32–0.34
Nauplius III0.36–0.40
Nauplius IV0.38–0.44
Nauplius V0.46–0.56
Protozoea I0.80–1.14
Protozoea II1.3–1.7
Protozoea III2.2–2.6
Mysis I3.2–3.8
Mysis II*4.0–4.4
Postlarva I4.0–5.0

* Probably Mysis III.

Williams (1955, 1955a), who studied estuarine habitats, noted that bottom areas of mud or fibrous peat are preferred by young P. setiferus, but that they occasionally occur on bottoms of sand or clay. He also concluded that the depth of water over these areas did not affect the numbers of shrimp, and that preferred areas usually had abundant cover, consisting primarily of organic litter and living vegetation. In controlled laboratory experiments, juvenile P. setiferus occurred more frequently on loose peat, sandy mud, and muddy sand than on shell sand and beach sand (Williams, 1958).

In Mobile Bay, Alabama, postlarval and juvenile P. setiferus (15 to 70 mm total length) were most abundant in water less than 0.6 m deep where the bottom contained large amounts of organic detritus (Loesch, 1965). Mock (MS), who sampled postlarval and juvenile white shrimp in an estuary at the shore and at a distance of about 15 m and 30 m from shore, encountered 98 percent of the white shrimp at the shore station. This shore area was charaterized by an organic mat or peat bottom (composed of more than 40 percent organics) bordered by emergent vegetation that was under water at high tide.

Various investigators, including Gunter (1950, 1961), Gunter, Christmas and Killebrew (1964), Williams (1955a), and Joyce (1965) have reported that postlarvae and juveniles of P. setiferus, P. aztecus, and P. duorarum penetrate toward fresh water in the order given. Gunter, Christmas and Killebrew (1964) recorded lower salinity limits of 0.42 for P. setiferus, 0.80 for P. aztecus and 2.50 for P. duorarum in the northern Gulf of Mexico. On the northeast coast of Florida the lower salinity limits were: P. setiferus, 0.26; P. aztecus, 0.46; and P. duorarum, 0.64 (Joyoe, 1965).

In Galveston Bay, Texas, Lee Trent and Jack Pullen (personal communication) on 23 April 1966, caught 9 P. aztecus, ranging in total length between 40 and 75 mm, in bottom salinity of 0.1. The bottom temperature was 28.0°C. On 12 July 1966 they captured 70 P. setiferus, 35 to 65 mm long, in a salinity of 0.7 and a temperature of 29.0°C. (There is some question as to the accuracy of the above low salinity records because they were determined from chlorinity analyses.)

At the other extreme, Gunter (1961) reported P.setiferus from a salinity of 41.3 and Hildebrand (1958) caught them, from 23 to 76 mm long, in Laguna Madre, Mexico in salinity of 47.96. Hildebrand (personal communication) stated: “In Laguna Madre of Texas, I have taken several specimens at a salinity of 62.4. However, this was in South Bay where the salinity might vary greatly with wind shifts and tidal patterns over relatively short periods of time. I also took it in salinities of 56.8 in the Upper Laguna Madre near South Bird Island. In general, I would agree with Simmons (1957) that it is generally rare at salinities greater than 40 and that the few that occur at higher salinities are strays or particularly hardy individuals which have survived a gradual increase in salinity.”

In general, results of laboratory experiments substantiate field observations. Griffith and Zein-Eldin (personal communication) recorded 80 percent survival of P. setiferus after 1 mo's exposure to salinities of 4.0 and 54.0. These specimens were between 50 and 100 mm total length; they were held at a constant temperature of 25°C and were gradually acclimated to the final salinities over a period of 4 wk.

In another experiment, when shrimp increased in average total length from 6 to 50 mm in 28 days, 80 percent of the experimental population survived salinities of 2.0 and 40.0. Temperatures were held constant at 25°C and the acclimation period was 48 h.

Zoula Zein-Eldin and George Griffith (personal communication) believe that the period of acclimation is extremely important in determining the extremes of salinity and temperature at which Penaeus spp. can survive.

Temperature extremes are not documented as well as salinity extremes. Weymouth et al. (1933) encountered P. setiferus in temperatures ranging from 9° to 31°C. Both P. setiferus and P. aztecus have survived a temperature of 36°C in a pond in North Carolina (Lunz, 1956). The total length ranged between 5.1 and 9.5 cm for P. setiferus and between 11.4 and 17.8 cm for P. aztecus. The same author (1958) stated that shrimp (presumably P. setiferus) in ponds survived temperatures exceeding 38°C.

Trent and Pullen (personal communication), after examining data from studies in Galveston Bay, reported the catch of 1 live but immobile P. setiferus (65 mm total length) on 28 January 1963, where bottom temperature was 2.6°C and salinity 12.8. Their records also show a catch of 531 P. setiferus (mean total length 85 mm) at bottom temperature and salinity of 35.5°C and 24.0 on 26 August 1963.

Rapidly decreasing temperature is known to kill P. setiferus. The rapidity of the change appears to be more important than the actual temperature (Gunter, 1941; Gunter and Hildebrand, 1951; Lindner and Anderson, 1956; Lunz, 1958). Iethal temperatures are not known but Gunter (1941) reported surface water in Copano Bay, Texas, to have reached a low of 4°C during the 1940 kill and Lunz (1958) mentioned 4.5°C.

Weymouth et al. (1933) and Gunter (1950) obtained a positive correlation between salinity and size of white shrimp, but Lindner and Anderson (1956) demonstrated that the size relation was with locality rather than salinity.

Gunter and Hildebrand developed a relation between Texas rainfall and Texas catch of P. setiferus. The highest correlation was between the catch of the year and the average annual rainfall of that year and the two previous years, with high catches associated with high rainfall values. They believed this relation was caused by salinity changes in the bays (Hildebrand and Gunter, 1953; Gunter and Hildebrand, 1954).

3.3 Adult phase

3.31 Longevity

No method has been developed to determine reliably the age of an individual shrimp. Lindner (1953) developed a technique for estimating age for restricted periods by mark-recapture experiments, and Lindner and Anderson (1956) demonstrated its usefulness in interpreting length-frequency distributions. Neither this technique, however, nor the von Bertalanffy growth formula, 1t = L (1-1-K(t-to)), can be used as a reliable indicator of shrimp age when the constant K changes as it does in P. setiferus between warm and cold periods. The method of Ursin (1963) may be an alternative.

Using information gained from maturity studies and length frequency plots, Lindner and Anderson (1956) demonstrated that P. setiferus lives at least 16 mo, but owing to high mortality, the number that live 2 yr or more is small with respect to the total population.

3.32 Hardiness

According to de Sylva (1954), P. setiferus is the least hardy, P. aztecus is the most hardy, and P. durorarum is intermediate. Field observations by the senior author while trawling, confirmed by David Harrington (personal communication), indicate P. duorarum to be the most hardy of the 3 species and P. setiferus the least. Butler (1962) observed that under laboratory conditions P. aztecus is more hardy than P. setiferus.

On the basis of size distribution in winter, Lindner and Anderson (1956) believed that juvenile and subadult P. setiferus are better able to withstand cold than the adults. Confirmation of this relation by experimental evidence is lacking.

Shrimp are extremely vulnerable to agricultural pesticides (Chin and Allen, 1957; Butler, 1962, 1963, 1966; Butler and Springer, 1963). Postlarval and small shrimp are generally more sensitive to pesticides than large shrimp; large white shrimp are less tolerant to some pesticides than large brown shrimp (Butler, 1962). Butler and Springer (1963, pp. 380, 381) stated, “Because shrimp, crabs, and other crustaceans are arthropods, like the insects, they understandably are sensitive to many of the chemical insecticides. Concentrations of heptachlor, endrin, and lindane in the range of 0.3–0.4 p.p.b. killed or immobilized half of the adult commercial brown and pink shrimp exposed in 48-h laboratory tests. Other chlorinated hydrocarbons, including DDT, chlordane, toxaphene, and dieldrin, showed similar effects at 1–6 p.p.b. In the laboratory, paralyzed individuals may live for days or even weeks, but in the struggle for survival in the sea this condition results almost immediately in death.”

3.33 Competitors

Little is known about the competition among the 3 species of Penaeus. P. setiferus and P. aztecus may be competitors during most or all of their lives (Broad, 1965). Where the 3 species occur off Galveston, Texas, however, the adults occupy quite distinct areas. Adult P. setiferus are most abundant on mud or sandy mud bottoms shoreward of 27 m, and adult P. aztecus are on similar bottoms seaward of 27 m. Adult P. duorarum occur most abundantly on shell or sandy shell bottoms.

On the Galveston Bay nursery grounds, the bulk of P. aztecus young are leaving or have left these grounds before most postlarval P. duorarum and P. setiferus have arrived. When the postlarvae occur together on the same nursery grounds, those of P. setiferus are closer to shore than those of P. aztecus (Loesch, 1965; Mock, MS). Postlarvae of P. duorarum seem to prefer grass flats. Williams (1955a) reported seasonal, size, and areal differences in the estuarine distribution of postlarvae and juveniles of the 3 species in North Carolina.

3.34 Predators

No exhaustive study of white shrimp predators has been undertaken. Predators on larvae, undoubtedly numerous, are unknown. Robert Temple (personal communication) has observed Penaeus mysis in the digestive tracts of arrow worms (Chaetognatha), but he was unable to determine whether the arrow worms had been feeding on the larval shrimp or whether they had accidently ingested the larvae while in the plankton net or while dying from the preservative.

Knapp (1949) examined 10,016 stomachs of 34 species of fishes from coastal waters of Texas between 7 June and 31 August 1948. Shrimp, principally P. aztecus, occurred in 61.8 percent of the 5,946 stomachs containing food. He reported shrimp as being the most widely used food between June and August, the season when P. aztecus is at peak biomass (Kutkuhn, 1962).

The following fish predators of Penaeus shrimp have been reported from the United States (areas 235 and 238 by Gunter (1945), Knapp (1949), Darnell (1958):

Carcharhinus leucas
Dasyatis sabina
Elops saurus
Megalops atlanticus
Anchoa mitchilli
Bagre marinus
Galeichthys felis
Ictalurus furcatus
Roccus mississippiensis
Lutjanus blackfordi
Pomatomus saltatrix
Rachyentron canadum
Caranx hippos
Coryphaena hippurus
Bairdiella chrysura
Cynoscion arenarius
Cynoscion nebulosus
Micropogon undulatus
Menticirrhus sp.
Pogonias cromis
Sciaenops ocellata
Scomberomorus cavalla
Scomberomorus maculatus
Istiophorus (Makaira)
Paralichthys lethostigma

We believe the above list of predators is incomplete. To us, Gunter's (1957, p. 102) remarks seem entirely appropriate: “It is a general observation of everyone working with shrimp that they are eaten by almost everything that is large enough to eat them, all the time. They are eaten by everything that lives around, in, or above the sea, including the lowly jellyfish. They are not only eaten but they are preferred.”

The defense reaction of Penaeus is a rapid flexing of the abdomen that causes the animal to dart backward. In large specimens the distance may be 1 m or more in less than 1 sec (observations of the authors).

3.35 Parasites, diseases, injuries, and abnormalities

The following parasites have been recorded from P. setiferus: Class Telosporidea: Nematopsis penaeus Sprague, 1954. Found in intestinal tract of host (Sprague, 1954); occurs as trophozoites, sporonts, and gametocysts (Kruse, 1959). Kruse (1959) reported 100 percent infection in Alligator Harbor and Apalachicola Bay, Florida. Shrimp have to be continually reinfected, or they lose the infections (Sprague, 1954; Kruse, 1959). Intestinal epithelium can be appreciably damaged (Sprague, 1954).

Class Cnidosporidea: Thelohania penaei Sprague, 1950. Found in reproductive organs of male and female (Sprague, 1950); occurs as spores and sporonts (Sprague, 1950). Viosca (1943) stated that in 1919 about 90 percent of P. setiferus in Louisiana were infected with a protozoan that destroyed their reproductive organs.

Class Cnidosporidea: Thelohania sp. Kruse, 1959. Found mainly in muscles, it also occurs in other organs as sporonts, pansporoblasts, and spores. Kruse (1959) recorded 10 percent infection in Alligator Harbor and Apalachicola, Florida, and considered this organism to be the cause of the “cotton” or “milk” condition in P. setiferus, P. aztecus and P. duorarum. “Cotton shrimp,” for esthetic reasons, are not acceptable for marketing in the United States.

Class Trematoda: Opecoeloides fimbriatus (Linton, 1934). Hutton et al. (1959, p. 19) found this parasite “Encysted in the hepatopancreas, the gonads, in the soft tissues of the head, around the mouth, around the stomach and in the soft tissues under the exoskeleton.” It occurs as metacercaria in Penaeus, adults in various species of fishes of the Family Sciaenidae (Kruse, 1959; Hutton et al., 1959). Hutton et al. (1959) found a single specimen in white shrimp from Apalachicola Bay, Florida. Kruse (1959), who worked in the same area, encountered it only in P. duorarum.

Class Cestoda: Prochristianella penaei Kruse (1959). Found by Kruse (1959) in “digestive gland and tissues surrounding digestive gland and stomach, blastocysts of larvae frequently penetrating wall of digestive gland.” Plerocerci occur in Penaeus, adults in the ray Dasyatis sabina (Aldrich, 1965). Kruse (1959) stated that in the north-eastern Gulf of Mexico 94.4 per cent of P. setiferus were infected with an average of 14.7 plerocerci. Aldrich (1965) reported 50 percent of the white shrimp in Galveston Bay, Texas, to be infected. Both incidence and intensity of infection increase with the size of the shrimp, up to a size of about 14 mm carapace length (Aldrich, 1965).

Class Cestoda: Polypocephalus sp. (= Parataenia sp.). Hutton (1964) listed this cestode as infecting P. setiferus as an intermediate host. He reported it to be present in numerous localities in Florida.

Class Nematoda: Contracaeum sp. Kruse (1959) found juveniles “In digestive gland and tissues surrounding digestive gland and stomach, not encysted.” The same author reported 5.5 percent infection in Alligator Harbor and Apalachicola Bay, Florida, and an average of 4 parasites per shrimp. Hutton, Ball and Eldred (1962) encountered 15.5 percent infestation and as many as 22 parasites in one specimen.

Dawson (1957) found maturing Balanus on 4 white shrimp.

3.4 Nutrition and growth

3.41 Feeding

From observations on Penaeus feeding in aquariums, the senior author is convinced that they are selective and particulate feeders. Shrimp search through the sand grains with their pereiopods and pass toward the mandibles only that which they choose. They appear to be particularly fond of polychaete worms.

3.42 Food

Studies on the food habits of shrimp have been hindered because their stomach contents are usually macerated and difficult to identify. Viosca (1920) and Weymouth et al. (1933) reported P. setiferus to be omnivorous. In reviewing the literature on the food of the 3 species of Penseus of the United States, Darnell (1958) and Broad (1965) reached the same conclusion. Gannibalism in captive P. setiferus was observed by Weymouth et al. (1933). Williams (1955), in discussing the food of the 3 species in North Carolina estuaries, stated that stomachs usually were full during summer, full or half-filled during fall, and nearly always empty in winter.

3.43 Growth rate

Linder and Anderson (1956) demonstrated, by means of mark-recapture experiments, that growth in P. setiferus along the coasts of the United States was much less when the temperature was below 20°C than when it was above. They developed Walford (1946) growth lines from successive 10-day intervals for the period of rapid growth. These data, converted to 30-day lines, had the following characteristics:

MalesY = 45.8 + 0.7427 XL = 178.0 mm
FemalesY = 56.4 + 0.7225 XL = 203.0 mm
CombinedY = 51.00 + 0.7322 XL = 190.45 mm

Klima (1963, and personal communication) calculated von Bertalanffy growth parameters from two mark-recapture experiments. For 7-day periods these parameters were:

 1963(Personal communication)
to-0.6-0.2
L224 mm214   mm
W87   g75.1 g
K0.060.09

3.44 Metabolism

Johnson and Fielding (1956) fed fresh fish to 2 groups of small white shrimp at a rate of 10 percent of their initial body weight per day. One group was held at 34 salinity and the other at 18.5 for 2 wk. Their results are summarized in the table given below.

P. setiferus are able to regulate total body fluid concentrations. Body fluids are hyperosmotic in brackish water and hyposmotic in hypersaline environments. Regulation appears to be more effective in low-salinity water. Also, the shrimp regulate the ionic concentration of Na, Cl, K, Ca and Mg in their serum (McFarland and Lee, 1963).

Love and Thompson (1966) studied the amino acid concentration in abdomens of P. setiferus and P. aztecus. The amino acids they found are shown in Table II. Nitrogen content did not vary seasonally in brown shrimp tails or offal, but certain amino acids did. Concentrations of a number of amino acids differed significantly between P. aztecus and P. setiferus, but the variation between analyses of P. aztecus on different dates indicates that the differences between species may not be truly significant.

In an earlier study, Jones, Moeller and Gersdorff (1925) reported tryptophane in the muscle of P. setiferus.

Boroughs, Chipman and Rice (1957, p. 82) stated that P. setiferus “accumulated strontium rapidly from sea water.”

3.5 Behaviour

3.51 Migrations and local movements

The young shrimp are planktonic in the offshore waters during their larval life and enter the estuaries as postlarvae about 7 mm total length. It is generally believed that these younger stages are not capable of extensive movement and that to reach the inside waters they must encounter favorable currents. Once in the estuaries, they make their way to the less saline, shallower areas, presumably by utilizing tidal currents. After growing rapidly for 3 or 4 mo, the young move into the deeper waters of the rivers and bays and then to sea. Movement out of the estuaries appears to depend on stage of maturity and temperature.

Lindner and Anderson (1956) described the general migration of adult white shrimp from shrimp tagged with Petersen discs. Klima (1963) reported on 2 experiments in Louisiana in which biological stains were used to mark white shrimp and found the same pattern of movement as described by Lindner and Anderson for tagged shrimp in that area.

The following account of white shrimp migrations has been taken from Lindner and Anderson (1956). The longest migration recorded was 360 mi (667 km) in 95 days, and the greatest time between marking and recapture was 257 days.

Salinity
Initial weight
(g)
Terminal weight
(g)
Gain
(g)
Gain
(%)
Food consumed
(g)
Conversion ratio
34.032.737.34.614.119.24.09:1
18.529.432.73.311.217.45.27:1

TABLE II

Average amino acid concentrations in tail meats of Gulf of Mexico Shrimp (adapted from Love and Thompson, 1966)

Amino acidsAverage amino acid concentrationSignificant species difference between samples taken on 20/2/64
P. a. aztecusP. setiferus
14/1/6320/2/6425/3/6320/2/64
 μ moles/mg Nμ moles/mg N 
Alanine3.703.644.264.36 
Arginine3.163.813.603.81 
Aspartic acid3.984.144.645.57*
Cystine/20.330.360.090.38 
Glutamic acid4.904.975.646.22*
Glycine6.356.196.456.96 
Histidine0.670.790.760.86 
Hydroxylysine0.050.030.010.04 
Hydroxyproline0.090.110.030.01*
Isoleucine1.862.022.132.59*
Leucine3.353.593.874.32*
Lysine2.823.523.113.46 
Methionine0.871.041.061.25 
Ornithine0.130.100.120.11 
Phenylalanine1.111.201.301.42 
Proline2.112.292.462.47 
Serine1.921.962.332.40*
Taurine0.470.310.570.65*
Threonine1.701.771.932.16*
Tryptophan0.39-0.45- 
Tyrosine0.770.850.740.89 
Urea0.070.080.16- 
Valine2.062.312.572.80*

* Indicates difference

After reaching outside waters, movements vary with size, locality, and season. Shrimp less than 130 mm, total length, did not migrate extensively, but remained adjacent to their nursery areas. Shrimp larger than 130 mm exhibited distinct migrations that varied with locality.

Atlantic coast: The white shrimp in this area migrate southward during the autumn and early winter and then move northward again in late winter and early spring. These movements parallel the coast, and do not extend into deeper water far from the coast. During late spring and summer movement is not pronounced.

Northern Gulf east of the Mississipi: All that is known of movement in this area is that during autumn and winter the shrimp move into deeper water and toward the mouth of the Mississipi River.

Northern Gulf west of the Mississipi River: The only definite movements in this area are offshore and onshore movements. The large shrimp move offshore and disperse during autumn and winter. Apparently the Mississipi River acts as a natural barrier.

Central Texas and northern Mexico: The migration in this part of the Gulf appears similar to that on the Atlantic coast, but the evidence is not conclusive. Indications are that the shrimp move from central Texas into northern Mexico during autumn and early winter.

There should also be a corresponding northward migration out of Mexico in the spring.

3.52 Schooling

Hildebrand (1954) stated that white shrimp school more extensively than related species.

The senior author believes that white shrimp of about the same age or length tend to aggregate in groups but that these aggregations do not possess the consistency through time generally attributed to a school of fish.

3.53 Responses to stimuli

Thermal

See section 3.16 for effect of temperature on spawning and 4.42 for lethal temperatures.

Lindner and Anderson (1956) found that P. setiferus moved from shallow to deeper water in response to unusual cold spells. They also uncovered evidence that the smaller shrimp moved back into shallower water as the water temperature increased.

Optical

Temple and Fischer (1965) demonstrated that penaeid larvae showed vertical diurnal migrations when the water column was vertically stable. Larvae moved into the surface layers in darkness and into deeper water during daylight.

4 POPULATION

4.1 Structure

4.11 Sex ratio

The sex ratio is 1:1.

4.12 Age composition

The mortality rate is high, and while some white shrimp may live more than 2 yr, the percentage is insignificant. Age composition of the catch consequently varies directly with recruitment and movement of the maturing shrimp into offshore waters.

The young enter the inshore fishery at an age of about 2 mo and the offshore fishery at about 3 or 4 mo.

4.13 Size composition

Size composition varies in the same manner as age composition.

The young enter the inshore fishery at a minimum total length of about 50 mm and the offshore fishery at a minimum total length of about 100 mm. Lindner and Anderson (1956) give an L of 203 mm for females and an L of 178 mm for males (see also 3.43).

The weights of large shrimp are greater in relation to length than are those of small ones. There is no appreciable difference in length-weight relations between sexes. Chin (1960) expressed the length-weight relation with the following equation:

Log W = -5.289 + (3.075) (Log L)

This equation agrees with the length-weight relation given by Anderson and Lindner (1958) until the shrimp reach a total length of 143 mm. Above this size, weights at comparable lengths given by Anderson and Lindner were greater than those of Chin (1960). Anderson and Lindner found a difference in length-weight relations between mature and immature shrimp; mature shrimp weighed more at a given total length. Chin believed that this factor might explain the differences between the 2 sets of data.

4.2 Abundance and density of population

4.22 Changes in abundance

White shrimp production peaked in the early 1940 s. Production in 1940 is estimated to have been about 65,000 metric tons, whole weight. At this time, intensive fishing for brown and pink shrimp had not started, and white shrimp were estimated to account for 95 percent or more of the total catch (Anderson, Lindner and King, 1949). Between 1945 and 1948, production of white shrimp declined and has not approached the high levels of the early 1940's since then. During the years for which we have reliable statistics (1957 to 1965, Table III), the catch has varied from 14,447 metric tons in 1957 to 36,188 in 1963. The cause of these fluctuations is not known.

TABLE III

United States white shrimp landings in metric tons, whole weight

YearEast coast, North Carolina to FloridaGulf coast, Florida to TexasTotal
19576,673  7,77414,447
19585,03217,98023,012
19595,81617,16722,983
19608,52219,82628,348
19616,36510,09316,458
19625,50416,18121,685
19633,29732,89136,188
19643,68330,72034,403
19657,39523,47030,865

In 1940, the white shrimp population in South Carolina and Georgia was decimated by a severe cold spell. In 1941, the return of landings to normal indicated that a normal crop may be produced by relatively few spawners (Linder and Anderson, 1956). Kutkuhn (1962) attributed the low 1957 landings of white shrimp in Louisiana to the effects of severe storms which struck the coast while the young of the spring spawning class were in the estuaries. Again, the fishery made a good recovery after 1 yr.

4.23 Average density

Kutkuhn (1962) indicated the 4-yr trend (1956 to 1959) in biomass of P. setiferus in the northern Gulf of Mexico to have been increasing to the east of the Mississippi River and decreasing to the west.

4.24 Changes in density

There are 2 periods of increased density on the offshore fishing grounds, one in late fall and the other in spring (Weymouth, et al., 1933; Lindner and Anderson, 1956; Kutkuhn, 1962).

4.3 Natality and recruitment

4.33 Recruitment

Rate of recruitment has not been determined. With some local variation, inshore recruitment starts in June and continues until the onset of cold weather (Lindner and Anderson, 1956).

4.4 Mortality and morbidity

4.41 Mortality rates

Klima (1963) gave an instantaneous total mortality rate of 0.92 for white shrimp off Louisiana from September through November. This is a 14-day rate of decline of 60 percent.

4.42 Factors causing or affecting mortality

See section 3.34 and 4.22

4.43 Factors affecting morbidity

See sections 3.23, 3.32, and 3.35

4.6 The population in the community and the ecosystem

After making an extensive survey of macrofauna on the white shrimp grounds in the Gulf of Mexico, Hildebrand (1954) listed the dominant organisms to be: White shrimp, Penaeus setiferus; blue crab, Callinectes danae; sea pansy, Renilla mulleri; Texas venus, Pitar texasiana; silver seatrout, Cynoscion nothus; Atlantic croaker, Micropogon undulatus; Atlantic threadfin, Polydactylus octonemus; and sea catfish, Galeicthys felis.

5 EXPLOITATION

5.1 Fishing equipment

5.11 Gears

The various gears used in the inshore fishery for white shrimp range from the modern trawl to primitive weirs and include trynets, pushnets, frame trawls, lift or drop nets, side frame trawls, seines, cast nets and dip nets. In the United States some shrimp are taken in estuaries for sale as bait, largely with a single 3- to 11-m otter trawl with a stretched mesh size of 3 to 5 cm. If the shrimp are to be kept alive, they are placed in a tank on the boat equipped with running sea water, or in a live box which is towed behind the boat. On shore, the live shrimp are kept usually in large bait boxes suspended in the water or in large holding tanks through which sea water is pumped (Inglis and Chin, revised by Baxter, 1966).

Most vessels fishing in offshore waters use a pair of 12-to 15-m flat or balloon otter trawls, but some use only one. Almost all boats use trynets, which are miniature trawls, to locate fishable concentrations of shrimp. A detailed description of trawling gear was given by Robas (1959).

In the early fishery in the United States, fishing was primarily with haul seines and cast nets. In Mexico, fixed traps predominated. Between 1912 and 1915, the otter trawl was introduced and by 1917, it had become the standard commercial gear. Practically all shrimp boats on the Atlantic coast were equipped with power winches by the mid-twenties, but with the exception of Texas, winches were not introduced into the Gulf until the late thirties (Johnson and Lindner, 1934; Anderson, Lindner and King, 1949). In the Gulf of Mexico, doublerig trawling was tried first in 1955, and was soon adopted by most offshore boats (Knake, Murdock and Cating, 1958).

5.12 Boats

Vessels of varied design, usually not exceeding 9 to 14 m in length, are used in the inshore fishery. Power is supplied by engines that burn gasoline or distillate. The boats are equipped usually with power winches and rope or wire towlines (U.S. Fish and Wildlife Service, 1958).

Vessels in the offshore fishery are predominantly Florida-type trawlers, which are described in detail by Cook and Lindner (1970).

5.2 Fishing areas

5.21 General geographic distribution

P. setiferus is fished along the Atlantic coast from Pamlico Sound, North Carolina to about Vero Beach, Florida (land areas 237 and 238) and in the Gulf of Mexico from Apalachicola, Florida to about lat. 23° N on the Mexican coast (land areas 235, 237, and 311). Between lat. 23° N and Tupilco, Tabasco, Mexico, there is no fishery. From Tupilco, however, the fishery extends eastward to about Champoton, Campeche. The 3 centers of abundance are in Georgia, Louisiana, and between Alvaro Obregón, Tabasco, and Isla del Carmen, Campeche (Hildebrand, 1955; Carranza, 1959; Anderson and Lunz, 1965; and Lindner, personal observations).

5.22 Geographic ranges

The accompanying map (Fig. 1) adapted from Hildebrand (1954), Lindner and Anderson (1956), Anderson and Lunz (1965), and Lindner (personal observations), delineates the primary fishing areas.

5.23 Depth ranges

The white shrimp has been recorded from depths down to 82 m, but it is most abundant on bottoms shoreward of 27 m (see sections 2.1 and 3.33).

5.24 Condition of grounds

See section 2.1.

5.3 Fishing seasons

White shrimp are harvested all year but peak production is in the autumn. Between 1956 and 1959, the greatest monthly catch in Texas waters was taken in September, about 63 percent of the catch was made during September and October and about 84 percent from August through November. The only other month of high production was May (Gunter, 1962). The greatest catch off the east coast of Florida is made from September through January and the peak is in December (Joyce, 1965).

5.4 Fishing operations and results

5.41 Effort and intensity

Fishermen frequently land mixed catches of brown, white and pink shrimp. In these instances, effort is reported only for the dominant species and not by individual species. As a result, there have been no reliable studies that require effort information on individual species.

Fig. 1

Fig. 1 Distribution and major fishing areas for Penaeus setiferus.

5.42 Selectivity

No critical data are available for P. setiferus on the selective properties of gear or effects of changes in mesh sizes but, presumably studies on the other 2 species would be applicable.

Market prices of all commercial penaeids in the United States are based on size; the largest shrimp command the highest price. Fishermen frequently fish in areas that yield larger shrimp in preference to areas with too many small shrimp. When large quantities of small shrimp are taken, it is not uncommon for them to be discarded either because they do not meet minimum size regulations, or because the fishermen do not want to bother with them.

Laws on minimum size are enacted by individual states and therefore vary.

Offshore shrimp fleets are highly mobile, and are moving continually from one location to another as abundance of the 3 commercially important species changes. During periods of peak abundance of one species, boats frequently concentrate in relatively small areas, leaving other areas and species unfished. At other times of the year, the fleet is dispersed over the entire fishing range.

5.43 Catches

See section 4.22.

Table IV gives United States shrimp production through 1940. It is estimated that white shrimp constituted more than 95 percent of these landings. The United States began collecting more detailed statistics on its Gulf coast landings in 1956 and expanded this coverage to the Atlantic coast fishery in 1957. Table III (section 4.22) gives the United States white shrimp landings since 1957. These landings do not include production from the bait fisheries, which in some areas is substantial. During 1964, for example, more than 850,000 lb (about 400,000 kg) of shrimp were taken for bait in Galveston Bay, Texas (Inglis and Chin, revised by Baxter, 1966). About 65 percent or 250,000 kg were white shrimp (Kenneth Baxter, personal communication).

TABLE IV

United States shrimp landings through 1940 in metric tons, whole weight (Power, 1960)

YearEast coast, North Carolina to FloridaGulf coast, Florida to TexasTotal
1889    337  3,767  4,104
1890    337  3,380  3,717
1897    284  3,081  3,365
1902  1,729  5,609  7,338
1908  2,584  5,835  8,419
1918  7,10114,67221,773
192310,76121,37132,132
192713,60431,24244,846
192815,10937,27152,380
192913,98435,25449,238
193011,88628,08339,969
193111,56432,18543,749
193210,18929,84640,035
193411,77642,34654,122
193615,22638,34853,574
193712,44551,63664,081
193812,50351,06863,571
193912,55854,60567,163
194010,29757,98668,283

6 PROTECTION AND MANAGEMENT

6.1 Regulatory (legislative) measures

In the U.S.A., each of the shrimp-producing States has its own legislation but all require licenses for fishing vessels. In Mexico, only members of legally authorized fishing cooperatives can fish commercially for shrimp (U.S. Fish and Wildlife Service, 1958; Lindner, 1957).

In the U.S.A., regulatory measures vary greatly between States and sometimes, even between counties within a State. The following types of regulatory measures are commonly imposed:

  1. Limitations on size and type of gear used;
  2. limitations on size of shrimp permitted to be landed;
  3. limitations on catch in inside waters;
  4. permanent and temporary closure of inside waters;
  5. temporary closure of outside waters within territorial limits.

6.2 Control or alterations of physical features of the environment

Mock (MS) demonstrated that the abundance of postlarval and juvenile shrimp is reduced greatly along bulkheaded portions of estuarine borders. He has also obtained data (personal communication) which show that silt from dredging and spoil banks kills submerged vegetation. Submerged vegetation is a preferred habitat of young Penaeus, and as the vegetation disappears from an area the number of shrimp decreases greatly.

7 POND FISH CULTURE

In general, P. setiferus is regarded as being well suited for pond culture. Attempts at culturing have been experimental, however, and there are no commercial pond culture operations at the present time.

In one of the earlier culture experiments conducted by Johnson and Fielding (1956), sexually mature P. setiferus that had been reared or held in dirt ponds spawned viable eggs when placed in a 21 × 9 × 12 m concrete tank filled with sea water. The resulting larvae were reared to postlarvae in 10 to 12 days. The shrimp were reared to a total length of 50 mm in the tanks in which they were hatched. Water in the tank was fertilized with a commercial inorganic fertilizer (7 parts elemental nitrogen; 9 parts phosphoric acid; 0 parts potash) to promote algal growth for larval food during early development. Later stages were fed daily on ground fish.

The work of Johnson and Fielding has not been repeated and subsequent workers have had to rely on postlarvae taken from the estuaries to stock their ponds. Recently, however, Cook (1969) developed a method for culturing white shrimp larvae under laboratory conditions. Although this method needs further modification before large-scale culture becomes practical, sufficient numbers of postlarvae were reared to stock a 0.05-ha (⅛-acre) pond. After the laboratory-reared shrimp had been in the pond 117 days, Ray Wheeler (personal communication) harvested 32 kg (70 lb) of shrimp with an average total length of 112 mm. Survival was 84 percent. Wheeler did not add supplemental food; instead he fertilized the pond water with chicken manure. During the first 35 days, the shrimp grew at a rate of 2.33 mm per day, but during the remainder of the experiment average growth was reduced to only 0.23 mm per day.

Lunz (1967) reported that white shrimp stocked in ponds as young adults in the spring reached sexual maturity the following spring, but they did not spawn. Personnel at the Bears Bluff Laboratories, Wadmalaw Island, South Carolina, have also succeeded in rearing white shrimp postlarvae from eggs spawned in the laboratory. Lunz (1967) said that some eggs hatched and 2 percent of the resulting larvae were reared to postlarvae.

Johnson and Fielding (1956) were troubled by excessive mortalities, as have been subsequent workers. One of the causes of mortality has been the presence of predaceous fish. Lunz and Bearden (1963) found that rotenone, a specific poison for fish, does not kill shrimp and other decapod crustaceans when applied in proper concentrations. They used 1.4 kg (3 lb) of powdered cube root with a 5-percent-rotenone content for each 1,233 m3 of water, giving a rotenone concentration of about 1.5 parts per million. Saponin, a poison contained in tea seed cake, is used for fish control in Asia, but Lunz and Bearden (1963) found it to be too expensive for general use, even though it worked satisfactorily.

8 REFERENCES

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