roy troll border art
nefsc banner
Technical Memoranda Reference Documents Classic Publications Contract/Grant Reports
CMER Publications Series Information Links and Contacts Annual/Biennial Lists
Web Manager Email Search Publications Publications Home Site Map
Tech Memo 121 APPENDIX A

Life History Synopses for Selected Fish Species Inhabiting the Hudson River Estuary

Understanding habitat requirements of the selected fish species in the Hudson River estuary requires an understanding of the distribution and environmental limitations for each life stage found in the estuary. A synopsis of the life history of each selected species reveals that a variety of habitats and regions of the Hudson River estuary are utilized; it also reveals some disagreement in the literature, as well as a general lack of information on specific habitat requirements for all life stages. Included in this appendix are 11 complementary figures (Figures A1-A11) for the 11 selected species which schematically present spatial distribution by life stage. References cited in this appendix are listed in the "References Cited" section of this document.


ATLANTIC STURGEON
Figure A-1

The Atlantic sturgeon, Acipenser oxyrhynchus, is an anadromous species of the Hudson River. The following account of life history is summarized from Bain et al. (1995). Adult Atlantic sturgeon live along the Atlantic coastline for approximately 10 yr before migrating into coastal rivers. Males enter the Hudson River in early April, before the females. Atlantic sturgeon do not spawn annually, with 2-5 yr between spawning events. Spawning occurs well upstream from the salt front; larvae are known to be intolerant of euryhaline environments.

Eggs are demersal and adhesive. The larvae remain close to the river bottom for some time. Juveniles are fairly evenly distributed in the Hudson River during summer, with their highest concentration between Kingston and Haverstraw Bay (Rkm 140 and 63, respectively). After summer, when water temperatures fall below 20°C, juveniles are found in high numbers between the Bear Mountain Bridge and the George Washington Bridge (Rkm 74 and 19, respectively). This tighter distribution is thought to represent an overwintering area for juvenile Atlantic sturgeon. Juveniles move back upstream in early spring, and do not migrate out of the Hudson River until 2-6 yr of age. Adults spend approximately 10 yr at sea before maturation and subsequent inland migration. Males and females mature at different ages, approximately 12 and 15 yr of age, respectively.


SHORTNOSE STURGEON
Figure A-2

The shortnose sturgeon, A. brevirostrum, is considered to be a nonmigratory, euryhaline fish. In the Hudson and other large rivers, adult shortnose sturgeon overwinter in deep polyhaline water downstream from the spawning grounds to which they will travel in the following spring when water temperatures reach 8-9°C (Dadswell et al. 1984). In the Hudson River, spawning occurs in April and May between Coxsackie and Troy (Dadswell et al. 1984; Hoff et al. 1988). Detailed information on spawning habitat is available for shortnose sturgeon of the Savannah River, South Carolina (Smith et al. 1993), which may or may not apply to those of the Hudson River. Adults are thought to move downstream in May and June, after spawning (Hoff et al. 1988).

Eggs of the shortnose sturgeon are demersal and adhesive (Dadswell et al. 1984). Larvae and juveniles are probably benthic, remaining in deep water where currents are strong (Dadswell et al. 1984; Hoff et al. 1988). As a result, little is known about the early life stages. In addition, identification of young specimens (eggs, larvae, and juveniles) is extremely difficult because of overall similarity to young Atlantic sturgeon (Hoff et al. 1988). Some workers (i.e., Hoff et al. 1988) believe that the larvae disperse downstream during summer, whereas others (i.e., Dadswell et al. 1984) believe that young shortnose sturgeon remain above the salt front until they reach 45 cm total length (TL). Upon attaining adult size (45-50 cm TL), shortnose sturgeon move downriver in fall, and back upriver in spring (Dadswell et al. 1984).

Sexual maturation is thought to be at 3-4 yr of age for males, and probably 6-8 yr of age for females, in the Hudson River (Dadswell et al. 1984). The age of maturation for females is based on age at first spawning. It is unknown how frequently shortnose sturgeon in the Hudson River spawn; in Canada, females spawn every 3 yr, and males every other year (Dadswell et al. 1984).


ALEWIFE
Figure A-3

The alewife, Alosa pseudoharengus, is an anadromous species of the Hudson River (Schmidt and Stillman 1994). Adult alewife spend most of the year in coastal Atlantic waters, migrating into the Hudson River (and other estuaries) to spawn. Alewife probably return to their natal river to spawn (Klauda et al. 1991). Alewife usually enter the Hudson River in early spring, prior to mid-May (Schmidt et al. 1988).

Spawning usually occurs in freshwater tributaries, in relatively shallow water with a slow current (Schmidt et al. 1988); in fact, the alewife is the only anadromous fish species commonly found in freshwater tributaries of the Hudson River (Schmidt and Stillman 1994). Eggs and larvae are not morphologically distinguishable from those of blueback herring (A. aestivalis), and for this reason, the two species are typically referred to as "river herring" (Dovel 1981; Schmidt et al. 1994). The role of blueback herring in tributaries is still unclear; however, because adult alewife are frequently sampled from freshwater tributaries during the spawning season, it has been assumed that most, if not all, of the eggs and larvae found in the freshwater tributaries are alewife (Schmidt et al. 1994). This contradicts earlier findings in which alewife eggs and larvae were presumed to be present in the main river channel (Boreman 1981). In addition to the differences in spawning location, larvae and eggs can also be distinguished by their temporal distribution, because alewife spawn about a month earlier than blueback herring (Hildebrand and Schroeder 1928; Schmidt et al. 1988).

Eggs are essentially pelagic, somewhat adhesive, and demersal in still water (Hildebrand 1963; Norden 1967; Lippson and Moran 1974; Klauda et al. 1991). In the Chesapeake Bay area, alewife larvae and juveniles may move further upstream to avoid intrusion of saltwater (Klauda et al. 1991). Larvae and juveniles remain in the freshwater tributaries of the Hudson River until June. At this time, juvenile alewife move out of the nursery areas of the tributaries and make their way downstream to the lower Hudson River and into the Atlantic Ocean (Schmidt et al. 1988), although capture of yearlings suggests some may overwinter in the estuary during the first year of life.

Alewife feed primarily on amphipods, mysids, copepods, small fish, and fish eggs (Leim and Scott 1966).


BLUEBACK HERRING
Figure A-4

The blueback herring, A. aestivalis, is an anadromous fish of the Hudson River (Klauda et al. 1991). Adults remain in coastal waters of the Atlantic Ocean and migrate upriver to spawn, as do alewife. Blueback herring usually spawn later in the spring than alewife, and in different habitat (Schmidt et al. 1988). Blueback herring prefer to spawn in relatively deep freshwater with swift currents on hard substrates of either gravel or sand (Schmidt et al. 1988; Klauda et al. 1991). It has been noted that this habitat preference is mainly seen in northern populations where blueback herring are sympatric with alewife, and, conversely, southeastern blueback herring spawn in lentic as well as lotic water (Klauda et al. 1991). It has been observed that blueback herring do not move as far upstream in tributaries as alewife (Loesch 1968, 1969), and recent studies in the Hudson River suggest that blueback herring spawn mainly in the main channel of the estuary, whereas alewife spawn more in tributaries (Schmidt et al. 1994). The single peak, seen in late May, in the temporal distribution of "river herring" eggs in the main channel (Boreman 1981) may therefore represent eggs of blueback herring.

Eggs of the blueback herring are pelagic, somewhat adhesive, and demersal in still water (Hildebrand 1963; Norden 1967; Lippson and Moran 1974; Klauda et al. 1991).

"River herring" larvae found in the main channel of the Hudson River estuary are thought to be blueback herring; larvae probably remain in nearshore habitat (Schmidt et al. 1994). Juveniles move downriver in July, later than alewife (Boreman 1981; Schmidt et al. 1988).

Food of blueback herring consists mainly of plankton, copepods, pelagic shrimp, and early life stages of small fishes (Scott and Crossman 1973).


AMERICAN SHAD
Figure A-5

The American shad, A. sapidissima, is a highly migratory species of the Hudson River, and is often cited as a classic example of an anadromous fish. Adults move into the Hudson River from Atlantic waters in early spring, usually beginning in March or April (Boreman 1981), depending on the water temperature of the river, which must be 12°C or above before the shad begin their run (Bigelow and Schroeder 1953). Adult American shad do not eat when running or spawning, and will not do so until they begin the postspawning downriver migration to the Atlantic, eating along the way (Bigelow and Schroeder 1953). Spawning occurs mainly at night (Bigelow and Schroeder 1953; Ross et al. 1993), in shallow freshwater of moderate current (Schmidt et al. 1988), and on various substrates (Bigelow and Schroeder 1953).

Eggs are demersal and nonadhesive (Bigelow and Schroeder 1953), and hatch after 2-17 days, depending on water temperature (Boreman 1981). Bigelow and Schroeder (1953) report that eggs raised in water at 12°C hatch between 12 and 15 days. Eggs are found in the spawning areas (Boreman 1981), and are not associated with any particular habitat type (Ross et al. 1993). In a 1974 study, egg abundance peaked in May (Boreman 1981); yolksac larval abundance has also been reported to peak in May (Schmidt et al. 1988). Yolksac larvae absorb their yolk in 4-5 days in water at 17°C (Boreman 1981). Larvae are reported to frequent riffle pools where water is of moderate depth and variable velocity and direction (Ross et al. 1993). Both feeding and yolksac larvae are planktonic; dispersal therefore occurs by passive transport (Boreman 1981; Schmidt et al. 1988). Juveniles are found downriver from the spawning grounds (Boreman 1981) beginning in June, with peak abundance in July (Schmidt et al. 1988). Juvenile habitat preference in the Hudson River seems to be positively correlated with depth, turbidity, and current velocity, possibly as an effect of food distribution (Ross et al. 1993). Most juveniles complete their migration from freshwater into the Atlantic by late fall or early winter (Bigelow and Schroeder 1953; Boreman 1981; Schmidt et al. 1988).

Adult American shad overwinter in the deep water of the Atlantic and Gulf of Maine (Boreman 1981). They move closer to their natal river in the spring, due to their strong homing ability (Boreman 1981). Adult American shad are euryhaline, but only enter freshwater to spawn (Bigelow and Schroeder 1953).


ATLANTIC TOMCOD
Figure A-6

The Atlantic tomcod, Microgadus tomcod, is a euryhaline fish of the Hudson River estuary. It is not considered to be migratory per se, but does show significant, seasonal, upriver/downriver movement within the estuary. Spawning of Atlantic tomcod takes place under ice, mainly from December to January (Bigelow and Schroeder 1953; Boreman 1981; Klauda, Moos, and Schmidt 1988; McLaren et al. 1988; Dew and Hecht 1994). The winter spawning occurs upriver mainly in fresh and possibly in brackish water (Boreman 1981; Klauda, Moos, and Schmidt 1988; Dew and Hecht 1994).

Eggs are demersal (Bigelow and Schroeder 1953; Boreman 1981; Klauda, Moos, and Schmidt 1988). The state of adhesion or nonadhesion of eggs is unknown, due to the difficulty of winter collection; conflicting opinions range from nonadhesive (Boreman 1981), to probably adhesive (Klauda, Moos, and Schmidt 1988), to adhesive (Bigelow and Schroeder 1953). Hatching occurs in freshwater (Dew and Hecht 1994) after 24-60 days in February and March (Klauda, Moos, and Schmidt 1988; Dew and Hecht 1994). Yolksac larvae reach peak abundance in mid-March, and post-yolksac larvae reach peak abundance in mid-April (Klauda, Moos, and Schmidt 1988). The yolksac larval period is approximately 4 wk, and the feeding larval period is approximately 6 wk (Boreman 1981). Larvae disperse downriver to Rkm 19-53 by mid-May (Klauda, Moos, and Schmidt 1988). The lower Hudson River is considered to be a nursery area for young Atlantic tomcod (McLaren et al. 1988). Juveniles are thought to peak in mid-May, mainly in the Tappan Zee and Yonkers regions (Klauda, Moos, and Schmidt 1988), although earlier reports show that juveniles did not appear until early August (Boreman 1981). They move upriver in mid-spring (Dew 1995), possibly to remain in brackish water as the salt front moves upriver (Klauda, Moos, and Schmidt 1988).

In the Hudson River, males and females both sexually mature between 11 and 12 mo, during their first fall (Boreman 1981; Klauda, Moos, and Schmidt 1988; McLaren et al. 1988). Adult Atlantic tomcod therefore spawn in their first year. Atlantic tomcod are not thought to move out of the Hudson River estuary during their life span, although they are found frequently in mouths of estuaries when not spawning (Bigelow and Schroeder 1953).


BAY ANCHOVY
Figure A-7

The bay anchovy, Anchoa mitchilli, is a coastal species which enters the lower Hudson River in April as adults (Woodhead et al. 1992). Adults are present in the lower estuary in high numbers in the summer, and are absent from the estuary in the winter (Woodhead et al. 1992). Egg collections suggest spawning occurs in the lowest regions of the Hudson River and probably out into coastal waters (Boreman 1981). Spawning is typically in water less than 20 m deep (Richards 1959); spawning activity in the lower Hudson River occurs from early June to mid-August and perhaps beyond, as suggested by a study of anchovy spawning in nearby Long Island Sound (Richards 1959). Since the minimum age at maturity is 2.5 mo at a size between 30 and 40 mm (Stevenson 1958), it is likely that bay anchovies spawn in their first year of life.

Eggs are pelagic (Klauda et al. 1991) and hatch in about 24 hr; yolksacs are absorbed in another 24 hr (Boreman 1981). Anchovy eggs have been collected in the Hudson River estuary up to Rkm 88 (Boreman 1981). The distribution of young anchovy shifts upriver as development progresses through summer. Post-yolksac larvae metamorphose in August and September (Woodhead et al. 1992). Juveniles in Chesapeake Bay prefer freshwater habitats (Klauda et al. 1991); this may also be the case for juveniles in the Hudson River as suggested by the upriver shift in distribution mentioned earlier. In the Hudson River, juvenile anchovy emigrate to sea in the fall; few remain in the estuary after November (Woodhead 1991).

Although no tagging studies have been conducted on Hudson River bay anchovy, studies elsewhere suggest that oceanic movements are limited to inshore-offshore migrations (Hildebrand 1963). Bay anchovy feed on detrital material and small planktonic animals in the Hudson River estuary (Boyce Thompson Institute for Plant Research 1977).


BLUEFISH
Figure A-8

Bluefish (Pomatomus saltatrix) are ocean spawners; larval and early juvenile development also occurs offshore. Bluefish first appear in estuaries as juveniles and, in the Northeast, usually arrive in the lower Hudson in late summer and fall (Boyle 1968). The distribution of larvae offshore is fairly well studied (Kendall and Walford 1979), but that of early juveniles is less known. Very little information is available on habitat requirements, food habits, or multispecies interactions in the oceanic phase. Juvenile bluefish generally appear in nearshore coastal waters in two waves, one in spring and another in summer, suggesting two spawning periods or a protracted spawning season offshore (Sargent and Boreman 1984).

In estuaries, juvenile bluefish are piscivorous, feeding on a wide variety of prey items (Marks and Conover 1993). Juvenile bluefish in the Hudson River feed on bay anchovy, white perch, American shad, river herring, and striped bass (Texas Instruments 1976b; Juanes et al. 1993).


LARGEMOUTH BASS
Figure A-9

The largemouth bass, Micropterus salmoides, is a freshwater-oligohaline, nonmigratory species inhabiting the Hudson River. When preparing to spawn, adult largemouth bass select appropriate sites in which to construct nests and to fertilize and deposit eggs. In the Hudson River, spawning and nesting habitat typically consists of protected coves and bays, and almost never exposed shoreline (Nack et al. 1993). Miller and Kramer (1971) found high mortality rates for eggs and larvae due to exposure to wind-induced waves, which explains why largemouth bass seem to prefer lentic habitat. Also, while specific effects of tidal action on developing eggs are unknown, stable water levels are associated with high recruitment (Von Geldern 1971). Nesting in coves and bays may slightly mitigate effects of tidal action. Temperature may be an important environmental cue for the timing of spawning because the early season nests seem to be in areas of warmer water (Nack et al. 1993).

Eggs are adhesive, sticking to one another in a mass and to the substrate upon which they are laid, such as gravel or roots (Breder and Rosen 1966). Male largemouth bass guard the nests, even after the eggs have hatched (Breder and Rosen 1966). Larvae and juveniles use the area around nesting sites as nursery habitat (Green et al. 1988; Green et al. 1989; Nack et al. 1993). Presumably, these preadult life stages remain in the tributaries where they would be protected from waves, unstable water levels, as well as some predators.

Adult largemouth bass also prefer lentic water in protected areas, especially in winter (Carlson 1992). Largemouth bass are believed to seek shelter from tide-affected areas in winter when their metabolic rates are low (Carlson 1992). Largemouth bass tend to leave overwintering sites when water temperature rises to 10°C (Nack et al. 1993).


STRIPED BASS
Figure A-10

Striped bass (Morone saxatilis) spawn in the fresh-brackish reach of the Hudson River, concentrating between Rkm 54 and 88, from early May through June (Boreman 1981). Striped bass eggs are semibuoyant (Hardy 1978). The yolksac larval stage runs 3-6 days, and the feeding (post-yolksac) larval stage may last 4 wk (Boreman and Fletcher 1993). The distribution of the early life stages in the river has been well documented (e.g., see Boreman and Klauda 1988), showing that the fish distribute both upriver and downriver as they develop. Timing of movement of juveniles out of estuarine nursery areas varies among stocks; in the Hudson River, age 0 fish move out of the river to estuaries in Long Island Sound and New Jersey. By age 1, these fish are participating in coastal migrations. Temperature is usually implicated in triggering migrations, but further studies relating movement and environmental conditions or prey availability seem warranted. Coastal movement of striped bass tagged in the Hudson River is extensive, but concentrated between Cape May and Cape Cod (McLaren et al. 1981).

Food habits studies conducted in the estuary (Texas Instruments, Inc. 1976a) suggest that age-0 striped bass feed primarily on harpacticoid, calanoid, and cyclopoid copepods, Gammarus spp., and chironomid larvae, progressing to fish as they age. Striped bass greater than 75 mm feed on bay anchovies, and striped bass greater than 116 mm feed on clupeids, Atlantic tomcod, mummichogs, Morone spp., and banded killifish. White perch, bluefish, Atlantic tomcod, largemouth bass, and smallmouth bass have been reported as potential predators on striped bass larvae (McFadden et al. 1978).


WHITE PERCH
Figure A-11

In the Hudson River, the white perch, M. americana, is a nonmigratory euryhaline species which is widely distributed throughout the river. Spawning occurs from April to June (Bigelow and Schroeder 1953; Klauda, McLaren, et al. 1988) or July (Boreman 1981), with peak egg deposition in mid-May to early June in the upper Hudson (Klauda, McLaren, et al. 1988). Spawning takes place mainly in freshwater (Englert and Sugarman 1988; Klauda, McLaren, et al. 1988) in a variety of protected habitats, such as shallow flats, embayments, and tidal creeks (Klauda, McLaren, et al. 1988).

Eggs are demersal and adhesive (Bigelow and Schroeder 1953), and hatch after only 1.5-2 days (Boreman 1981). Yolksac larvae are found in the same areas as the eggs, probably as a result of the short duration of the larval stages (3-5 days) (Klauda, McLaren, et al. 1988). Feeding larvae are more widely distributed due to their higher mobility, and disperse downriver in July (Klauda, McLaren, et al. 1988). This finding on post-yolksac larval distribution conflicts with earlier sampling data from the 1970s which indicated that both egg and larval stages are widely distributed in the Hudson, with larval stages found between Rkm 39 and 201 (Boreman 1981). Juveniles first appear in June, dispersing downriver and into the shorezone during the end of summer; juveniles were mainly found close to shore in October, but then moved into deeper water by December (Klauda, McLaren, et al. 1988).

Adult white perch sexually mature at age 4 in males, and age 5 in females (Klauda, McLaren, et al. 1988). There is no known habitat preference for adults; they are widely distributed in the Hudson River in both brackish and freshwater habitats (Klauda, McLaren, et al. 1988), but remain in the river for their entire life span (Boreman 1981).