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NOAA Technical Memorandum NMFS-NE-161

Demersal Fish and American Lobster Diets in the Lower Hudson - Raritan Estuary

Frank W. Steimle, Robert A. Pikanowski, Donald G. McMillan, Christine A. Zetlin, and Stuart J. Wilk
National Marine Fisheries Serv., 74 Magruder Rd., Highlands, NJ 07732

Web version posted April 30, 2002

Citation: Steimle FW, Pikanowski RA, McMillan DG, Zetlin CA, Wilk SJ. 2000. Demersal Fish and American Lobster Diets in the Lower Hudson - Raritan Estuary. US Dep Commer, NOAA Tech Memo NMFS NE 161; 106 p.

Information Quality Act Compliance: In accordance with section 515 of Public Law 106-554, the Northeast Fisheries Science Center completed both technical and policy reviews for this report. These predissemination reviews are on file at the NEFSC Editorial Office.

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Characterizing the demersal fish food web in the Hudson-Raritan Estuary is important for understanding specifically how this estuary is used by fishery resources. Knowledge of fish food webs and essential fish forage resources of the estuary can support habitat management decisions. Little is known about diets of the community of fish and the American lobster (Homarus americanus) that inhabit this estuary, although it is a major estuarine complex in the Northeast that continues to support fisheries. To gain insight into trophic and habitat functions in this estuary, the diets of the most abundant demersal fish species and the American lobster were examined. These predators were collected by trawl in various parts of the Hudson-Raritan Estuary over six seasons, July 1996 through November 1997.The most widely preyed-upon taxa were crustaceans, such as: small or juvenile decapods (e.g., sevenspine bay or sand shrimp (Crangon septemspinosa), hermit crabs (Pagurus spp.), juvenile Atlantic rock crabs (Cancer irroratus), lady crabs (Ovalipes ocellatus), and mud crabs (Xanthidae)); the mysid Neomysis americana; and several amphipod species. Clam siphons, primarily from the northern quahog (Mercenaria mercenaria) and Atlantic surfclam (Spisula solidissima), were commonly preyed upon by winter flounder (Pseudopleuronectes americanus), as well as by scup (Stenotomus chrysops) and spot (Leiostomus xanthurus) during some seasons. The diets of common fish and the American lobster in the human-stressed Hudson-Raritan Estuary are similar to those in other, less-stressed estuaries in the Middle Atlantic Bight.


The Lower Hudson-Raritan Estuary (hereafter, the Estuary), located at the mouths of the Hudson, Raritan, and Navesink-Shrewsbury Rivers (New Jersey - New York), is the polyhaline part of a major, urban, estuarine complex in the Northeast. The Estuary has supported diverse and productive commercial and recreational fisheries (MacKenzie 1992). Many of these fisheries are gone or operate at a reduced level because of low resource abundances, harvest regulations, and/or habitat degradation.

The Estuary has been characterized as one of the most human-altered on the East Coast (Wolfe et al. 1996). Although some sources of habitat alteration or degradation in the Estuary (e.g., point-source discharges and marsh filling) are being largely controlled through regulation, other sources (e.g., nonpoint-source discharges and toxic substance spills) continue with little effective control, and new activities have the potential for adverse effects (Palermo et al.1998). Despite these alterations, the Estuary is still used by a diversity of aquatic species (Wilk et al.1998).

To conserve and restore the Estuary's fishery resources, there is a need for community- or ecosystem-level information on the status and function of the Estuary's various habitats and associated species to provide advice for policy decisions on conflicting uses of the Estuary. Characterizing fish and American lobster diets in the Estuary is critical for understanding the value and habitat sources of various prey taxa in the estuarine food web. Knowledge of food webs and key predator-prey relationships is important for habitat-use policy development (Hartman and Brandt 1995).

Although broadscale trophodynamic studies have been conducted in many other Middle Atlantic Bight estuaries, e.g., Long Island Sound (Richards 1963), central New Jersey (Festa 1979), Delaware Bay (de Sylva et al.1962), and Chesapeake Bay (Homer and Boynton 1978), as well as offshore in the New York Bight (e.g., Sedberry 1983; Bowman et al.1987), the Hudson-Raritan Estuary has never had such an effort. Only the middle Hudson River part of the Estuary (near Indian Point, New York) has received attention for general dietary analysis (Gladden et al.1988), although there have been focused dietary analyses of a few species such as striped bass (Morone saxatilus) and juvenile bluefish (Pomatomus saltatrix). Also, Stehlik et al.(in preparation) examined the diets of several species of crabs within Raritan Bay, which complements the present study. Little else has been reported on the diets of the demersal fishery resource community of the Estuary, except for some brief incidental or anecdotal observations (Hall 1894; Merrill 1904; Breder 1922b; NJDEP 1975; Lynch et al.1977; Lawler, Matusky & Skelly Engineers 1980; Conover et al.1985).

To address this information deficiency, we report on the results of a seasonal study of the diets of common demersal fish species and the American lobster (Homarus americanus) collected in various parts of the Estuary. This study is roughly modeled on Festa's (1979) study for a shallow, south New Jersey estuary, and is intended to complement that effort, as well as the cursory dietary information in Able and Fahay (1998). These results are also compared to a comprehensive summary of most other dietary studies for the same predators in other Middle Atlantic Bight estuarine or coastal areas. A brief summary of the life history and habitat of major prey is also included because many of the habitat issues that managers have to deal with involve potential perturbations to the health and availability of common prey. This report is intended to be a ready source of trophic and habitat-use information for subtidal habitat management within this estuary.


The strata and blocks (areas) that were sampled to collect fish and American lobster for stomach content analysis covered most of the Estuary (Figure 1), but were restricted to depths greater than 3.0 m because of survey vessel operational factors. The habitat characteristics of these strata are summarized in Table 1.

Six seasonal sampling periods were used to collect specimens for diet analysis: 1) July 8-12, 1996; 2) October 7-10, 1996; 3) January 27-30, 1997; 4) April 22-29, 1997; 5) August 18-28, 1997; and 6) November 17-20, 1997. In addition, a special collection of scup (Stenotomus chrysops) was made during June 9-11, 1997; data on scup from that collection are included in the August 18-28, 1997, sampling period. For each sampling period, approximately 40 blocks were randomly selected from about 200 possible blocks within the nine sampling strata.

Fish and American lobster samples were collected by a semiballoon otter trawl that had a 8.5-m headrope, 10.4-m footrope, 10.2-cm stretch-mesh nylon net, and a 3.5-cm stretch-mesh liner in the cod end. This trawl was towed for 15 min at ~3.7 km/hr (2 knots). Hydrographic data (i.e., depth, salinity, temperature, and dissolved oxygen) were collected after each successful tow using a "Hydrolab Surveyor 4" multisensor. [Use of trade names is for information only, and does not represent endorsement by NMFS.] Details of the overall trawl survey are available in Wilk et al.(1998).

After the trawl was retrieved, the catch was sorted to species, weighed (g), and measured (0.1 cm). Then, up to about 10-15 specimens of each nonplanktivorous fish species were selected for analyses, as available. If available, additional samples were also collected for each apparent size class of a species. As feasible, the stomachs of large fish such as skates, dogfishes, and adult striped bass were examined in the field, or the eviscerated stomachs of such fish were placed individually in labeled plastic bags and quickly frozen. Small specimens were also bagged and frozen whole for later laboratory analysis.

To examine the diets in the field or laboratory, the contents of each stomach were carefully emptied onto a gridded petri dish. The total stomach bolus volume was visually estimated by a side-by-side comparison with a set of variable-diameter, volume-calibrated (cm3) cylinders. The bolus was separated and examined (by dissecting microscope, if necessary), then the stomach items or prey were segregated into the lowest identifiable taxon, counted, and measured for length (if possible), and finally, the proportion of each prey taxon or other item to the total stomach volume was estimated visually using the petri dish grid. Items or prey were identified to the lowest level practical using numerous taxonomic references, e.g., Bigelow and Schroeder (1953), Gosner (1973), and Weiss (1995). The findings of clam siphons in winter flounder (Pseudopleuronectes americanus) and a few other predators prompted the collection of whole specimens of larger bivalve mollusks which commonly occurred in the area in order to examine their siphons for characteristics that could identify the specific source of the siphons that were found in the stomachs. These characteristics were used to develop a rough guide to siphons to improve the level of prey species identification.

The young-of-the-year (YOY) stages of most fish species (either as predator or prey) examined in the analyses were identified mostly using Bigelow and Schroeder (1953), Fitz and Daiber (1963), and a prepublication draft of Able and Fahay (1998). The transition lengths at 50% maturity, used to segregate juvenile and adults of certain fish species as part of the diet analysis, were based on O'Brien et al. (1993).

A literature review of target predator diets in the coastal Middle Atlantic Bight, the area between Cape Cod and Cape Hatteras, was used to create summary tables of the diet of each predator for comparison with results of the present study. In these tables, prey were listed by their relative overall importance using several ranking metrics, as available from the document source: mean percent frequency of occurrence (FO), mean percent contribution to total stomach content volume (TV), mean percent contribution to total stomach content weight (TW), mean percent contribution to total stomach content dry weight (TDW), mean percent contribution to total number of individual items in the stomach (TN), and an index of relative importance (IRI; FO x TV, or, FO x TW). Those comparative data available as FO and TV are the same as those used in the present study. The two "fresh condition" variables of TV and TW are nearly equivalent (i.e., 1 g of prey as "fresh" weight approximates 1 cm3 of prey as "fresh" volume) for most prey such as crustaceans, polychaetes, fish, shell-less mollusk meat, etc., but not for heavy-shelled prey (e.g., sand dollars and mollusks in the shell) consumed whole (Steimle et al.1994).

Our results for diets focus on dominant prey used by predators found in the Estuary. Dominant prey are generally defined as those contributing five or more percent to total stomach content volume, but prey of fishery management significance, such as juvenile fishery species, are also noted. The results are also presented in the order of predator sample abundance. For each predator, the results of this study are followed by the summary of the results of other studies for comparative purposes. Because of the relatively large number of predators considered in this predator-community-focused report, this strategy of reporting by predator sample abundance keeps relevant information together for each predator, and should be most convenient to users of this report. Summaries focused on common prey, with a brief review of their life history and habitat associations, are also presented.



Winter Flounder (Pseudopleuronectes americanus)

Hudson-Raritan Estuary Results

This species is a common, year-round inhabitant of the Estuary, and was collected in a range of sizes (6.1-45.0 cm total length (TL), mean of 20.0 cm) and strata, except in the central and coastal parts of Lower Bay, Stratum 3 (Figure 2). The 710 winter flounder which were examined ate 80 distinct, identifiable prey taxa, although only about 20 benthic invertebrates occurred at a relatively high FO. Endobenthic and epibenthic polychaetes (21+ species), amphipods (14+ species), and mollusks (10+ species) dominated the diet. This flounder also ate a range of food types, from plant detritus to algae to tunicates, including planktonic copepods (e.g., Pseudodiaptomus coronatus), suprabenthic mysids and the amphipod Gammarus lawrencianus, as well as the epibenthic and endobenthic invertebrates. Typically, smaller species, earlier life stages, and/or fragments of larger benthic species were eaten. Some larger bivalve mollusks, e.g., northern quahogs (Mercenaria mercenaria) and Atlantic surfclams (Spisula solidissima), were important in the diet, but only their siphons were nipped or torn off by this nearly toothless predator. The blue mussels (Mytilus edulis) that were found in the diet, e.g., during April 1997 (Table 2a), were all spat less than 1 cm in length. The decapod crabs that were eaten Atlantic rock crab (Cancer irroratus), blue crab (Callinectes sapidus), lady crab (Ovalipes ocellatus), and Libinia sp. were all juveniles. A diversity of tube-dwelling amphipods were also eaten, especially Ampelisca abdita. Although several polychaete species were identified as being eaten, only the tube-dwelling Asabellides oculata and Sabellaria vulgaris, and the blood worm Glycera sp., were relatively common in the diet, i.e., occurring in the top 20 prey ranked by FO (Table 2a). The percentage of empty stomachs that were found ranged from 2.9% in April 1997 to 42.2% in January 1997; this variable generally ranged between 6.7 and 16.9% for other sampling periods (Table 2a).

Unidentified organic matter (i.e., detritus) ranked as the most frequently occurring diet item, followed by northern quahog siphons, Ampelisca abdita, Atlantic surfclam siphons, and unidentified polychaetes or their fragments (Table 2a). The TV of prey or prey type for all samples was again dominated by unidentified organic matter, Atlantic surfclam and northern quahog siphons, the mysid Neomysis americanus (hereafter, "Neomysis"), unidentified clam siphons, A. abdita, and unidentified polychaetes (Table 2a). Other prey individually represented a TV of less than 3%. As with FO, there was a high degree of intersample variability (Table 2a).

For most prey, there were only small seasonal variations in the degree of their use by winter flounder, but for some prey, there were obvious differences. For example, there was minimal use of clam siphons during January 1997 (Table 2a). At the same time, there was increased use of Neomysis and nemerteans. Seasonal predation peaks for other prey varied annually, i.e., there was relatively high predation during one summer sampling, but not the other summer sampling, covered in this survey (e.g., predation on juvenile Atlantic rock crabs and Asabellides oculata; see Table 2a).

Other prey or items found in winter flounder stomachs in lesser quantities were: green and red algae; anthozoans; nematodes; bryozoans; gastropods (juvenile Crepidula sp., Lacuna vincta, Epitonium sp., Astyris lunata, and Nassarius trivittatus); bivalve mollusks (Solemya velum, Nucula sp., Mulinia lateralis, Tellina agilis, softshell (Mya arenaria) siphons, and Lyonsia hyalina); polychaetes (Phyllodoce sp., Eteone sp., unidentified polynoids, Nephtys sp., Nereis succinea, N. grayi, Nereis sp., unidentified capitellids, Asychis elongata, Clymenella torquata, Spiochaetopterus oculatus, Sabellaria vulgaris, Diopatra cuprea, Lumbrineris sp., Arabella iricolor, Pectinaria gouldii, Melinna cristata, Nicolea venustula, and Pherusa affinis); arachnids (juvenile Limulus polyphemus); copepods (unidentified calanoids, harpacticoids, and cyclopoids, and the calanoid Pseudodiaptomus coronatus); cumaceans (Diastylis sp.); tanaids (unidentified); isopods (Edotea triloba and Cyathura sp.); amphipods (Lembos websteri, Ericthonius sp., Gammarus sp., Jassa falcata, Hippomedon serratus, Orchomenella sp., Photis sp., Phoxocephalus holbolli, Stenothoe sp., and Parametopella sp. (cypris?)); mysids (Heteromysis formosa); decapod crustaceans (Pagurus sp., P. longicarpus, xanthids (Dyspanopeus?), juvenile blue crabs, juvenile Libinia sp., and juvenile Ovalipes ocellatus); echinoderms (juvenile Echinarachnius parma); tunicates (Molgula sp.); and sand, shell hash, organic detritus, and manmade artifacts such as coal granules and synthetic fibers.

Winter flounder diet changed with size/growth. This shift in use of common prey was generally from small crustaceans (mysids and amphipods), polychaetes, and detritus by smaller fish, to more bivalve mollusk siphons by larger fish (Table 2b). Winter flounder diet was examined for seasonal shifts in prey use as related to flounder size and maturity. Because of small sample sizes for each of the four size groups portrayed in Table 2b, the samples were pooled into two groups: juvenile (less than 20 cm TL; Table 2c) and adult (greater than or equal to 20 cm TL; Table 2d). In the summer-fall, juvenile winter flounder focused their feeding on northern quahog and Atlantic surfclam siphons, an amphipod (i.e., Ampelisca abdita or A. vadorum), a tube-dwelling polychaete (Sabellaria vulgaris), and detritus, although Neomysis became important as prey in the winter (Table 2c). Other prey were relatively evenly used during most seasons or showed no seasonal pattern of use. For adults, the list of commonly eaten prey was condensed, with only four distinct prey being notable, and seasonal sample sizes were more irregular and often inadequate (Table 2d). Again, clam siphons were the dominant prey. The large bloodworm Glycera sp. and juvenile Atlantic rock crabs were the only other prey with any seasonal peaks.

Some studies of the winter flounder diet have shown that the diet closely reflects environmental conditions and prey availability in the areas in which the fish are collected (Frame 1974; MacPhee 1969). The winter flounder diet in this study also showed differences in prey use that varied among sampling strata, although sample sizes were small for some strata, particularly for the channel habitats, Strata 7-9 (Table 2e, Table 2f). Some prey (e.g., Glycera sp.) were eaten in similar proportion by juveniles and adults from the same strata areas of the Estuary. Other prey (e.g., Neomysis, Crangon septemspinosa (hereafter, "Crangon"), and Gammarus sp.) were found in stomachs of juveniles or adults, but not both. The prey of juvenile winter flounder among different strata suggest no habitat-related patterns (Table 2e). There was no specific association of prey with channels (Strata 7-9), nor with the western or eastern areas, with the possible exception of the polychaetes Glycera sp. and Sabellaria vulgaris and northern quahog siphons in the western Strata 1-3, and Atlantic surfclam siphons in eastern Strata 4 and 6 (Table 2e). Predation by juveniles and adults on northern quahog siphons appears restricted to less-saline, western Strata 1-3 and 6, and predation on Atlantic surfclam siphons occurs in marine eastern Strata 4 and 5 and in channel Strata 7 and 8, as might be expected from the Atlantic surfclam's salinity preferences.

Comparisons with Other Diet Studies

Other winter flounder dietary studies in and near the Estuary, or within the coastal Middle Atlantic Bight, found a similar diet to that reported here, i.e., opportunistic predation on benthic invertebrate macrofauna, especially polychaetes and amphipods, and on zooplankton by the smallest winter flounder sizes (Table 3). However, there was an unusually high degree of molluscan siphon nipping in this estuary compared to what has been reported elsewhere (Table 2 & Table 3; Lawler, Matusky & Skelly Engineers 1980; Stehlik and Meise 2000). A lesser degree of molluscan siphon nipping by winter flounder has been also reported in Canada (Medcoff and McPhail 1952), Cape Cod Bay (Gilbert and Suchow 1977), Long Island Sound (Carlson 1991), and near Woods Hole, Massachusetts (Frame 1974; Lux et al.1996), and in a few other studies (Table 3), however. It has been assumed that this siphon nipping is nonlethal to the mollusks, which can be fishery resources in their own right, and that the siphons regenerate (Irlandi and Mehlich 1996).

Windowpane (Scophthalmus aquosus)

Hudson-Raritan Estuary Results

Windowpane from YOY to adult (range of 2.5-35.0 cm TL, mean of 20.7 cm) are a year-round inhabitant of this estuary. Five hundred seventy windowpane were examined from all areas, although slightly greater quantities were available from the channels, especially in and near Raritan Channel, Stratum 9 (Figure 3). At least 37 prey taxa were identified in their diet. This prey spectrum included two mysid species, three or more decapod crustacean species, seven amphipod species, two or more copepod species, eight mollusk species, nine identifiable species of larval or juvenile fish, and some miscellaneous, nonprey items (green algae to coal fragments). This prey spectrum included a mix of benthic, suprabenthic, and pelagic species.

Despite the overall diversity of prey consumed, windowpane have a relatively focused diet. By FO for all samples, Neomysis was the dominant prey at 65.9% (range of 33.7-93.3%). It was followed in importance by Crangon at 31.7% (range of 23.6-53.0%) and the suprabenthic amphipod Gammarus lawrencianus at 9.5% (range of 0.8-39.0%). The other prey were eaten at a low FO (i.e., less than 5%). The percentage of empty stomachs ranged from 2.0% in July 1996 to 33.7% in January 1997, and was between 10 and 24% in other sampling periods (Table 4a).

The TV paralleled the FO. Neomysis made up 57.1% of the overall diet by TV (range of 17.8-70.1%), with Crangon contributing 29% (range of 21.3-47.7%). Most other prey individually represented less than 0.1% of TV, although higher values occurred during some sampling periods (Table 4a).

Other prey or items found in windowpane stomachs in lesser quantities were: green algae; hydroids; nemerteans; gastropods (Lacuna vincta, juvenile Crepidula sp., Nassarius trivittatus, and Astyris lunata); bivalve mollusks (Mulinia lateralis, Nucula sp., unidentified, and blue mussel spat); cephalopods (unidentified squid); polychaetes (unidentified); copepods (unidentified); cumaceans (unidentified); amphipods (Corophium sp., Jassa falcata, Stenothoe sp., Hippomedon serratus, and Unciola sp.); mysids (Heteromysis formosa); decapod crustaceans (Pagurus longicarpus, Palaemonetes vulgaris, and unidentified zoea); fish (unidentified juvenile flounder, unidentified juvenile fish, juvenile Atlantic menhaden (Brevoortia tyrannus), juvenile herring (Alosa), juvenile red hake (Urophycis chuss), juvenile cunner (Tautogolabrus adspersus), Menidia sp., juvenile Atlantic croaker (Micropogonias undulatus), and juvenile sand lance (Ammodytes sp.)); and sand and coal pebbles.

There was seasonal variability in the consumption of some prey (e.g., the use of Neomysis peaked during the summer). The use of Crangon peaked in the winter-spring, although it was a major prey in July 1996 samples (Table 4a). G. lawrencianus was mostly consumed in the fall, especially in 1996, as was the red copepod Pseudodiaptomus coronatus.

There was a clear shift evident in prey use with windowpane growth (e.g., from Neomysis as overwhelmingly dominant for windowpane less than 20.0 cm TL, to Crangon for windowpane at larger sizes, although Neomysis was dominant at all sizes (Table 4b). Small fish (e.g., Anchoa sp.) also become more important for the larger-sized fish.

The results suggest some differences in prey use among strata and regions (Table 4c). Neomysis seems to be the basic prey in the Ambrose Channel to Verrazano Narrows area (Strata 6 and 7). Crangon, on the other hand, seems to be more often eaten in the central-western areas of the Estuary (i.e., Strata 2, 3, 8, and 9). Other prey constituted an insignificant proportion (a TV of less than 10%) of the diet in most areas, except in Strata 4 and 5 (the marine shoals) where small or juvenile fish were eaten. Windowpane abundances were highest in channels (Figure 3) where Neomysis might be most abundant; see the "Forage Base" section for a discussion of the habitat of Neomysis.

Comparisons with Other Diet Studies

No previous focused studies of the diet of this species are known for this estuary, although Breder (1922b) commented that stomach contents of a few specimens that he examined "consisted of crustacean remains, probably schizopods [mysids]." In general, other studies of the diet of this species in the Middle Atlantic Bight found mysids (especially Neomysis), Crangon, and "nekton" (i.e., small fish and squid) to be primary prey (Table 5), but smaller-sized windowpane also ate copepods. For the continental shelf, Langton and Bowman (1981) reported 40-60% of the windowpane that they had examined had empty stomachs, but mysids and shrimp continued to dominate the diet offshore. The results of the present study are consistent with those of other studies and with Bigelow and Schroeder's (1953) general summary of the diet, except for the relatively high use of G. lawrencianus as prey in the present study.

Little Skate (Raja erinacea)

Hudson-Raritan Estuary Results

Little skate (mostly adults) were commonly found throughout this estuary during most seasons, except the summer (Figure 4; Wilk et al.1998). The stomachs of 332 little skate (range of 33.0-49.0 cm TL, mean of 43.2 cm) were examined. Over 50 prey taxa or items, which ranged from green algae to a variety of small fish, were identified in the little skate diet. These prey taxa included 11 decapod crustaceans, 6 amphipods, 5 polychaetes, 8 mollusks, 10 identifiable fish, and miscellaneous prey or items (Table 6).

The most frequently found prey, overall, was Crangon at an FO of 82.8% (range of 77.2-92.9%). This prey was followed by juvenile or small Atlantic rock crabs at an FO of 49.5% (range of 7.1-75.3%), which were often found in a soft-shell stage, then by Neomysis at an FO of 16.3% (range of 6.1-28.5%) and Ovalipes ocellatus at an FO of 10.9% (range of 1.2-36.4%). The remaining prey had overall FOs of less than 10% (Table 6), with few empty stomachs.

The TV parallels the FO, with Crangon having 29.6% (range of 20.3-90.1%) of the TV, Atlantic rock crabs having 18.6% (range of 4.7-38.1%), and other prey having less than 10%, with the exception of the October 1996 sampling period when O. ocellatus had 15.6% (Table 6). A number of juvenile blue crabs were also eaten (Table 6).

Other prey or items found in little skate stomachs in lesser quantities were: unidentified green algae; hydroids; nematodes; nemerteans; gastropods (Lacuna vincta, Nassarius trivittatus, and Astyris lunata); bivalve mollusks (blue mussels, Mulinia lateralis, northern quahog siphons, and unidentified); polychaetes (Lumbrineris sp., Spiochaetopterus oculatus, Arabella iricolor, Pherusa affinis, Diopatra cuprea, and unidentified); copepods (Pseudodiaptomus coronatus); cumaceans (unidentified); isopods (Cirolana concharum, and Cyathura sp.); amphipods (Leptocheirus pinguis, Hippomedon serratus, Unciola sp., Ampelisca abdita, and unidentified); decapod crustaceans (unidentified, xanthids, Pagurus pollicaris, P. longicarpus, Palaemonetes vulgaris, Dichelopandalus leptocerus, and Axius serratus); stomatopods (Squilla empusa); fish (Raja sp. egg case fragments, juvenile rock gunnel (Pholis gunnellus), juvenile windowpane, northern searobin (Prionotus carolinus), unidentified searobins, sand lance, smallmouth flounder (Etropus microstomus), goby (Gobiosoma sp.), northern pipefish (Syngnathus fuscus), juvenile red hake, juvenile winter flounder, and juvenile silver hake (Merluccius bilinearis)); and sand, wood fragments, and human artifacts such as coal granules, iron rust flakes, and plastic particles.

Although little skate tended to be most common in this estuary in the cooler months, and sample sizes are relatively small in the summer, there appears to be a possible predation emphasis on Atlantic rock crabs and Neomysis during the cooler months (Table 6).

Comparisons with Other Diet Studies

No previous studies of the diet of this species are known for this estuary. However, the diet of this species has been studied elsewhere, both on the Middle Atlantic Bight continental shelf, and within other bays and estuaries (Table 7). These studies also show that small crustaceans dominate the little skate diet; with skate less than 20.0 cm TL eating small crustaceans (e.g., copepods, mysids, and amphipods such as Unciola irrorata, Gammarus annulatus, Leptocheirus pinguis, and Monoculodes edwardsi), and with larger skate eating more decapod crustaceans, especially Crangon, Cancer sp., Dichelopandalus leptocerus, and hermit crabs (Pagurus sp.). However, squid and small fish (e.g., sand lance, butterfish (Peprilus triacanthus), "herring" (Alosa sp.?), searobins, juvenile flounder, and red hake) were also eaten (Table 7). The diet of little skate from the Estuary (Table 6) is consistent with these other study results, and with the general dietary summaries reported in Nichols and Breder (1927) and Bigelow and Schroeder (1953).

Scup (Stenotomus chrysops)

Hudson-Raritan Estuary Results

Scup, mostly juveniles, were found from spring through fall in the Estuary and were relatively widespread in distribution, although with a tendency to be collected more often in the northern areas (Figure 5). The stomachs of 254 scup (range of 8.0-24.0 cm FL, mean of 12.9 cm) were examined. At least 39 items or prey taxa were identified in their stomachs, including 8 polychaetes, 7 amphipods, 6 decapod crustaceans, 6 mollusks, 2 mysids, and other taxa (e.g., hydroids). The majority of these prey were benthic, except for mysids and Gammarus lawrencianus (Table 8).

The dominant items in the diet by FO were unidentified organic matter at 35.8% (range of 21.3-46.1%), Neomysis at 32.3% (range of 17.3-50.0%), bivalve mollusk remains at 14.3% (range of 1.3-26.7%), G. lawrencianus at 16.8% (range of 0.0-48.3%), Crangon at 15.2% (range of 3.9-30.7%), unidentified polychaetes at 14.2% (range of 6.7-35.5%), and Ampelisca abdita at 10.1% (range of 0.0-18.0%) (Table 8).

The contribution of prey to the overall TV parallels that to the overall FO in the same order of contribution (Table 8). There were few empty stomachs.

Other prey or items found in scup stomachs in lesser quantities were: unidentified hydroids; unidentified nemerteans; gastropods (juvenile Crepidula sp., unidentified, and eggs); bivalve mollusks (Tellina agilis and Nucula sp.); polychaetes (Paranaites speciosa, Asabellides oculata, Sabellaria vulgaris, Pectinaria gouldii, Phyllodoce sp., Pherusa affinis, and Nereis sp.); copepods (Pseudodiaptomus coronatus and unidentified calanoid); cirripeds (Balanus sp.); tanaids (unidentified); isopods (Cyathura sp.); amphipods (unidentified, Orchomenella sp., Photis sp., caprellids, Unciola sp., and Corophium sp.); mysids (Mysidopsis bigelowi); decapod crustaceans (xanthid crabs, juvenile blue crabs, and unidentified); and fish (silversides (Menidia sp.) and unidentified).

There were few, notable, interannual or seasonal differences in the diet of this basically warm-season species, with the possible exception of predation on G. lawrencianus in 1996 that was not evident in 1997 (Table 8).

Comparisons with Other Diet Studies

Within this estuary, the only previous known data on the scup diet is from the unpublished, preliminary 1976 results of the senior author, who examined 13 juvenile fish from Strata 1, 3, and 4. He found that the mostly frequently consumed prey were: the polychaete Asabellides oculata and copepods in Sandy Hook Bay, polydorid polychaetes and the dwarf surfclam Mulinia lateralis off Staten Island, and copepods and blue mussel spat on Romer Shoal (Stratum 4).

Michelman (1988) found that the juvenile scup diet in Rhode Island varied seasonally, but was still generally focused on benthic invertebrates, such as polychaetes (e.g., maldanids, Nephtys sp., Nereis sp., and Pherusa affinis), small decapod crustaceans (Pagurus sp. and other crabs), Neomysis, amphipods (Leptocheirus pinguis and others), as well as mollusks, a burrowing anemone (Ceriantheopsis americanus), and fish eggs and larvae.

Most other studies found that scup less than 15 cm FL ate small invertebrates such as copepods, polychaetes, amphipods, decapod crustaceans (especially juvenile Atlantic rock crabs), and squid (Table 9); a number of qualitative or summary reports have found the same (Baird 1873; Peck 1896; Nichols and Breder 1927; Hildebrand and Schroeder 1928; Bigelow and Schroeder 1953; Allen et al.1978). Linton (1901) and Sedberry (1983) found that the diet of scup gradually shifted with growth or size from small pelagic crustaceans to a variety of benthic taxa. The results of the present study are basically consistent with these other results, and show a strong reliance on benthic macrofauna and detritus as prey.

Summer Flounder (Paralichthys dentatus)

Hudson-Raritan Estuary Results

This species was most commonly collected during the summer and throughout the Estuary, but especially along the New Jersey shore (Figure 6; Wilk et al.1998). The stomachs of 229 summer flounder (range of 13.8-69.0 cm TL, mean of 36.0 cm) were examined. Over 35 prey species or items were identified in their diet, including juvenile or small adults of 12 species of fish, 5 species of decapod crustaceans, Neomysis, and other taxa (Table 10). Crangon with an FO of 49.5% (range of 34.4-78.0%) and Neomysis with an FO of 19.8% (range of 0.0-33.6%) were most frequently eaten. Unidentified fish were next with an FO of 13.2% (range of 0.0-14.0%), and juvenile Ovalipes ocellatus were prominent in the August 1997 stomach samples (Table 10).

The FO ranking was also followed by the TV ranking, with Crangon having a TV of 29.4%, and Neomysis having a TV of 11.4% (Table 10). The percentage of empty stomachs ranged from 10 to 50%, with the highest levels being found in the winter-spring period.

Other prey or items found in summer flounder stomachs in lesser quantities were: unidentified algae; hydroids; bryozoans; gastropods (Crepidula sp. and Nassarius trivittatus); bivalve mollusks (blue mussel spat, Mulinia lateralis, Ensis directus, Nucula sp., and Tellina agilis); polychaetes (Sabellaria vulgaris and unidentified); copepods (unidentified calanoid); isopods (Cyathura sp.); amphipods (caprellids, Gammarus lawrencianus, and Ampelisca abdita); decapod crustaceans (juvenile blue crabs, Pagurus longicarpus, and unidentified); and fish (juvenile scup, cunner, rock gunnel, juvenile searobins, juvenile weakfish (Cynoscion regalis), Menidia sp., juvenile striped searobin (Prionotus evolans), juvenile black sea bass (Centropristis striata), northern pipefish, juvenile Alosa herring, and juvenile grubby (Myoxocephalus aenaeus)).

Summer flounder were mostly collected in the spring and summer (Table 10), so seasonal shift could not be examined. There were few notable dietary differences between 1996 and 1997, although in 1997 summer flounder made greater use of O. ocellatus and unidentifiable juvenile flounder as prey. Most (85%) of the summer flounder examined were 30 cm TL or more, and probably not YOY. Despite the small sample size for YOY summer flounder, their diet differed little from that of larger fish: Crangon and Neomysis dominated the diet, with small Ovalipes and fish being of notable importance (Table 10).

With the number of samples being few (i.e., less than 30 samples per stratum), and with the distribution of samples among strata being small, the results of interstrata comparisons were inconclusive, although there was a suggestion that Crangon were eaten commonly everywhere except in the Romer Shoal and Ambrose Channel areas (Strata 4 and 7). Neomysis were mostly found in stomachs examined from deeper channels (Strata 8 and 9) and near the Verrazano Narrows (Stratum 6), but also within Sandy Hook Bay (Stratum 1). The latter observations perhaps reflected some recent feeding in the unsampled Sandy Hook and Earl Naval Channels, located between Strata 1, 2, and 4.

Comparisons with Other Diet Studies

No previous studies of the diet of this species are known for this estuary.

In general, YOY summer flounder prey upon small fish (e.g., silversides, mummichog (Fundulus heteroclitus), bay anchovy (Anchoa mitchilli), and sticklebacks), and Palaemonetes, Crangon, and Neomysis shrimps (Table 11). The species is highly opportunistic, but its diet shifts ontogenetically, from small crustaceans at smaller sizes, to fish prey at larger sizes. The diet of the predominantly YOY and juvenile summer flounders examined in the Estuary, dominated by crustaceans and small fish (Table 10), is consistent with other studies (Table 11), and with the generalizations of Hildebrand and Schroeder (1928), Ginsberg (1952), and Bigelow and Schroeder (1953), which were often based on small or ambiguous sample sizes.

Red Hake (Urophycis chuss)

Hudson-Raritan Estuary Results

Red hake were commonly collected in channels and the deep area below the Verrazano Narrows (Gravesend Bay, Stratum 6; Figure 7) and during most seasons (Wilk et al.1998). The diet of 166 red hake (range of 4.3-39.0 cm TL, mean of 19.0 cm) was examined. These fish were primarily juveniles and were most frequently collected during cooler seasons. At least 33 prey species were identified in the diet, including 7 decapod crustaceans, 9 amphipods, Neomysis, 7 juvenile fishes, and other taxa from algae to mollusks. Most prey were benthic species.

Crangon with an FO of 77.6% (range of 56.3-100.0%), Neomysis with an FO of 31.7% (range of 0.0-48.4%), Gammarus lawrencianus with an FO of 20.9% (range of 0.0-100.0%), and unidentified organic detritus with an FO of 10.6% (range of 0.0-20.6%) dominated the diet.

Crangon dominated the diet's TV at 39.0% (range of 23.3-50.0%), followed again by Neomysis at 15.7% (range of 0.0-30.3%) (Table 12). The other prey were infrequently found in the stomachs, and few stomachs were found empty. The inadequate samples in 1996 and during warmer months (Table 12) prevent analysis of seasonal or interannual variation in the diet of this species.

Other prey or items found in red hake stomachs in lesser quantities were: green algae; hydroids; bivalve mollusks (Nucula sp., Tellina agilis, blue mussel spat, and unidentified); polychaetes (unidentified and Pherusa affinis); copepods (Pseudodiaptomus coronatus and unidentified calanoid); isopods (Edotea triloba); amphipods (Phoxocephalus holbolli, Unciola sp., Ampelisca abdita, Corophium sp., Jassa falcata, Stenothoe sp., Hippomedon serratus, and unidentified); decapod crustaceans (juvenile Libinia sp., Pagurus longicarpus, juvenile Ovalipes ocellatus, Palaemonetes vulgaris, and unidentified); fish (juvenile silver hake, juvenile red hake, smallmouth flounder, juvenile searobin, juvenile weakfish, juvenile cunner, unidentified juvenile flounder, and skate (Raja sp.) egg case fragments); and wood fragments.

Comparisons with Other Diet Studies

The diet of red hake from the Estuary (Table 12) is consistent with other dietary studies for the species, with crustaceans being primary prey. The only previous, quantitative study of the diet of this species in Raritan Bay examined 45 subadults of this species in spring 1976 within Sandy Hook Bay and off Staten Island (Steimle, unpubl. data). That diet was dominated (i.e., a TV of 92-100%) by Crangon. This result is consistent with Breder's (1922b) earlier comment that the few red hake that he looked at in Sandy Hook Bay in summer 1921 were "crammed full of large prawns"; these "prawns" were further defined as being Crangon in Nichols and Breder (1927).

In the nearby New York Bight apex (outside the mouth of the Estuary), over 1,000 red hake were examined and found to prey most commonly on Crangon, various polychaetes (mostly Pherusa affinis and Nephtys incisa), Neomysis, and benthic amphipods (Steimle 1985, 1994) (Table 13). Hildebrand and Schroeder (1928) observed that red hake that were caught off Sandy Hook had gorged on sand lance. In general, the summary of other studies (Table 13) and the treatise by Bigelow and Schroeder (1953) show that juvenile red hake eat a variety of small benthic and zooplanktonic invertebrates, but primarily crustaceans. Steiner et al.(1982) reported that juvenile red hake use shelter during the day (such as living sea scallops, Placopecten magellanicus) and leave this shelter to feed at night. As red hake grow, larger crustaceans such as decapods increase in importance in their diet, and some fish are also eaten (Table 13). Adult red hake were rarely collected within the Estuary (Wilk et al.1998).

Weakfish (Cynoscion regalis)

Hudson-Raritan Estuary Results

Weakfish were another summer-fall inhabitant of the Estuary and were collected mostly in or near channels, especially in Stratum 9, Raritan Channel (Figure 8). The stomachs of 197 weakfish (range of 7.5-54.0 cm TL, mean of 17.7 cm) were examined. Over 20 prey species or items were identified in the diet, but they were dominated by crustaceans and a few juvenile or small fish. Crangon and Neomysis were the most frequently eaten prey, with only Gammarus lawrencianus and digested fish (probably bay anchovy) being of any relative importance (Table 14). There do not appear to be any consistent interannual differences in the diet, although there were pulses of the consumption of Neomysis, bay anchovy, and juvenile silver hake in the diet during certain sampling periods (Table 14).

Other prey or items found in weakfish stomachs in lesser quantities were: unidentified hydroids; gastropods (Nassarius trivittatus); polychaetes (unidentified); crustaceans (unidentified); copepods (Pseudodiaptomus coronatus); amphipods (Corophium sp. and Unciola sp.); decapod crustaceans (Dichelopandalus leptocerus, juvenile Ovalipes ocellatus, juvenile Atlantic rock crabs, and juvenile blue crabs); fish (juvenile weakfish, juvenile Atlantic menhaden, butterfish, juvenile unidentified flounder, and juvenile windowpane); and human artifacts such as cellophane.

Comparisons with Other Diet Studies

The only previous information on the diet of this species known for this estuary are comments by Breder (1922b) that, when he examined a few adult weakfish from Sandy Hook Bay, he found that they had eaten fish such as Atlantic menhaden [juveniles?] , silver perch (Bairdiella chyrsoura), and anchovies, and squid and "prawns" [Crangon]. Another cursory diet examination by Lynch et al.(1977) of 25 juvenile fish from the Raritan River (western boundary of the Estuary) also noted that weakfish there also ate Crangon and fish. Within the upper Hudson River Estuary (above Manhattan Island), Gladden et al.(1988) reported that weakfish generally ate "fish and macroinvertebrates."

The summaries of the results of other weakfish studies (Table 15) and the generalized summary of Bigelow and Schroeder (1953) show that the diet of this species can vary substantially among estuaries. That is, it can be dominated by Crangon or small fish (especially bay anchovy and juvenile weakfish) in some estuaries, but by mysids (mostly Neomysis) or amphipods (e.g., Gammarus sp.) in others. The earliest studies listed in Table 15 were less precise in defining prey, but the "shrimp," "prawns," or "mysids" that they noted are almost certainly Crangon and Neomysis, and suggest that there does not appear to be any substantial shift in dominant prey over the decades, at least in the past century. Other weakfish diet studies were not listed in Table 15 because of limitations or the general nature of their information, e.g., Eigenmann (1902), Linton (1901), Tracy (1910), Nichols and Breder (1927), Hildebrand and Schroeder (1928), Lascara (1981), and Grecay (1990). The pattern of weakfish predation within the Estuary seems to be typical and focused on both Crangon and Neomysis, but small fish (e.g., bay anchovy, butterfish, and weakfish) and Gammarus sp. amphipods are also important (Table 14 and Table 15).

Spotted Hake (Urophycis regia)

Hudson-Raritan Estuary Results

Spotted hake of all size and age classes were collected commonly during the warmer months within the Estuary and mainly in channels, especially Raritan Channel (Stratum 9, Figure 9). The 162 spotted hake (range of 6.5-33.0 cm TL, mean of 18.3 cm) which were examined ate 30 prey taxa, ranging from hydroids to fish. The most frequently eaten prey were crustaceans (i.e., Crangon, Neomysis, and Gammarus lawrencianus) and small fish (Table 16). The copepod Pseudodiaptomus coronatus was frequently eaten in half of the sampling periods. Few empty stomachs were found. Crangon dominated the overall stomach volumes with a TV of 45.7% (range of 31.3-60.9%) (Table 16).

Other prey or items found in spotted hake stomachs in lesser quantities were: unidentified nematodes; bivalve mollusks (unidentified, Nucula sp., blue mussel spat, and juvenile Pitar morrhuanus); polychaetes (unidentified, Nereis sp., and Pherusa affinis); sipunculids (unidentified); crustaceans (unidentified); copepods (unidentified); amphipods (unidentified, Ampelisca abdita, Jassa falcata, Hippomedon serratus, Unciola sp., and Ericthonius sp.); decapod crustaceans (juvenile Atlantic rock crabs, Ovalipes oculata, Pagurus sp., Dichelopandalus leptocerus, and Palaemonetes sp.); and fish (juvenile silver hake, juvenile red hake, juvenile searobins, and smallmouth flounder).

Comparisons with Other Diet Studies

No previous studies of the diet of this species are known for this estuary.

In general, other studies show that spotted hake usually eat larger epibenthic crustaceans and small fish (Table 17). Among the crustaceans eaten, Crangon, Neomysis, copepods, other decapod shrimp, and crabs were prominent in the diet of this species. The variety of fish identified in these other studies included bay anchovy and sand lance among others. This diet spectrum is consistent with Bigelow and Schroeder's (1953) review, the species' diet south of Cape Hatteras (Burr and Schwartz 1986), and with the results of the present study (Table 16).

Striped Searobin (Prionotus evolans)

Hudson-Raritan Estuary Results

Adults and juveniles of this species were collected mostly during the summer months, and in or near channels or within Sandy Hook Bay (Figure 10; Wilk et al.1998). The 153 samples of striped searobin (range of 4.5-47.2 cm TL, mean of 21.4 cm) which were examined ate 34 identifiable prey taxa, but most frequently preyed upon Crangon, Neomysis, and other crustaceans, and upon small or juvenile fish. Of interest was the relatively frequent occurrence of small, approximately 1-3 mm, coal granules or pebbles in their stomachs (Table 18). The TV was dominated (45.8%, range of 37.4-71.4%) by Crangon (Table 18). The diet was similar for 1996 and 1997 (Table 18).

Other prey or items found in striped searobin stomachs in lesser quantities were: unidentified hydroids; gastropods (unidentified, Nassarius obsoletus, and N. trivittatus); bivalve mollusks (Nucula sp., Mulinia lateralis, and Ensis directus); cephalopod (unidentified squid); polychaetes (unidentified); crustaceans (unidentified); copepods (unidentified and Pseudodiaptomus coronatus); isopods (Edotea triloba); amphipods (unidentified, Corophium sp., and Unciola sp.); mysids (Heteromysis formosa); decapod crustaceans (xanthid crabs and unidentified crab fragments); fish (smallmouth flounder, juvenile windowpane, juvenile anchovy, juvenile grubby, unidentified juvenile flounder, juvenile searobin, juvenile black sea bass, and juvenile stargazer (Astroscopus sp.)); and sand.

Comparisons with Other Diet Studies

There is only one other study of the diet of this species known for this estuary. Manderson et al. (1999) examined 35 stomachs of this species from shallow water in Sandy Hook Bay (near Stratum 1) and its Navesink River tributary, at its southern border. They reported an FO of 68% of YOY winter flounder in the searobin's diet, although Crangon and other crustaceans were the primary prey.

A summary of most other quantitative studies of the diet of this species from different areas shows that the diet was also based on crustaceans (e.g., Crangon, Neomysis, copepods, amphipods, and juvenile crabs) and small or juvenile fish (e.g., winter flounder, striped and northern searobins, scup, windowpane, bay anchovy, Menidia, northern pipefish, and probably others) as available (Table 19). Other, more generalized discussions of their diet, e.g., Bigelow and Schroeder (1953), also note a broad spectrum of prey in the diet of this species, including crabs, amphipods, squid, bivalve mollusks, polychaetes, small fish (herring and winter flounder), and algae. In Richards et al.'s (1979) Long Island Sound study, they reported that the prey of age 1+ searobin varied with habitat type (i.e., prey eaten on sandy bottoms were different from prey eaten on muddy bottoms). For example, on sandy bottoms, the razor clam (Ensis directus) was important. They also found that some predation showed no habitat-related differences (e.g., on Neomysis, Crangon, and Ovalipes ocellatus and other crabs), and concluded that the diet of the adult striped searobin when at smaller sizes although having a great deal of overlap with the sympatric but smaller northern searobin tended to reduce competition for food by focusing on larger prey that were less specific in their habitat preferences. The results of the present study are consistent with the findings of other studies; although, again, one or more 2-5 mm diameter pebbles of coal or charcoal were observed in about 5% (range of 3-17%) of the stomachs (Table 18).

Northern Searobin (Prionotus carolinus)

Hudson-Raritan Estuary Results

This small species (range of 5.1-20.4 cm TL, mean of 15.1 cm) was collected mostly during the summer, and mainly in the eastern areas of the Estuary, e.g., between Verrazano Narrows and Sandy Hook Bay (Figure 11; Wilk et al.1998). One hundred three northern searobin stomachs were examined, and over 20 prey taxa were identified, which were mostly crustaceans. The reoccurring prey group of Crangon, Neomysis, and Gammarus lawrencianus were most frequently found in the stomachs. The contribution of prey to TV parallels their contribution to FO, although juvenile Atlantic rock crabs were of added importance to the diet of the large, August 1997 collection sample (Table 20). Coal pebbles were also found in these stomachs, but only during one collection, and then at an FO of 25% for the 87 fish examined (Table 20).

Other prey or items found in northern searobin stomachs in lesser quantities were: hydroids (unidentified); nematodes (unidentified); bivalve mollusks (blue mussel spat); polychaetes (unidentified); copepods (Pseudodiaptomus coronatus); isopods (Edotea triloba); amphipods (Corophium sp., Ampelisca abdita, and Leptocheirus pinguis); mysids (Heteromysis formosa); decapod crustaceans (Pagurus longicarpus); fish (juvenile smallmouth flounder, juvenile striped searobin, and juvenile black sea bass); and unidentified organic matter.

Comparisons with Other Diet Studies

No previous studies of the diet of this species are known for this estuary.

Some results of other studies of the diet of this predator show that, like its sibling species, the striped searobin, the northern searobin also preys principally upon crustaceans, with Crangon, Neomysis, amphipods, and copepods being prominent in the diet, but fish are eaten to a lesser degree (Table 21). This dietary pattern was also reported by Hildebrand and Schroeder (1928) and Bigelow and Schroeder (1953). The smaller adult size of the northern searobin, compared to the striped searobin, is a logical explanation for the difference in the use of fish (although juvenile herring, winter flounder, weakfish, bay anchovy, and others are reported as prey), and perhaps for the slightly greater use of smaller macrofauna such as polychaetes and cumaceans. In Long Island Sound, Richards et al. (1979) reported on the diet of YOY and older northern searobins, and despite some ambiguity in their results, the YOY of this species appeared to prey principally upon Neomysis and copepods, based on numbers eaten. Larger fish were more focused on amphipods, isopods, and small decapod crustaceans as prey. Mann (1974) found that diet of this species varied with sediments and water depth. The summary of results (Table 21) also shows that the diet of northern searobin from this estuary (Table 20) is consistent with other studies (Table 21).

Striped Bass (Morone saxatilus)

Hudson-Raritan Estuary Results

Striped bass of small-to-medium size (range of 13.5-65.0 cm FL, mean of 33.2 cm) were generally only collected by trawl within the Estuary during the fall-winter, especially in western areas of the Estuary: Gravesend Bay (Stratum 6) and channels (Figure 12; Wilk et al.1998). The 81 striped bass which were examined ate a diversity of prey, with greater than 20 identifiable species. The diet was dominated by a variety of small or juvenile fish and crustaceans (Table 22). Many stomachs per collection (up to 100%) were empty. Crangon again led in the diet with an FO of 62.3% (range of 54.5-75.9%) and TV of 50.3% (range of 15.0-100.0%). All other prey occurred or contributed less than 5% to TV, except Neomysis (Table 22).

Other prey or items found in striped bass stomachs in lesser quantities were: polychaetes (Nephtys sp.); isopods (Cirolana sp.); amphipods (unidentified and Gammarus lawrencianus); mysids (Heteromysis formosa); decapod crustaceans (Axius serratus); stomatopod (Squilla empusa); fish (rock gunnel, juvenile searobin, juvenile unidentified flounder, juvenile conger eel (Conger oceanicus), juvenile Urophycis sp., northern pipefish, bay anchovy, striped anchovy (Anchoa hepsetus), juvenile winter flounder, and juvenile grubby).

Comparisons with Other Diet Studies

There are no data on the diet of striped bass from within this part of the overall Hudson-Raritan Estuary. However, Lawler, Matusky & Skelly Engineers (1980) and Gardinier and Hoff (1982) did report on the striped bass diet in the Hudson River, 50 km north of the Verrazano Narrows. There they found that juveniles, less than 20 cm FL, fed on a mix of freshwater and marine organisms, including Gammarus and other amphipods (e.g., Corophium, Leptocheirus, and Monoculodes), insect larvae, copepods, isopods (e.g., Cyathura sp.), polychaetes, small decapod crustaceans (Crangon and mud crabs), and some small fish. While larger individuals were almost totally piscivorous, preying on river herring, Atlantic tomcod (Microgadus tomcod), bay anchovy, white perch (Morone americana), and killifish, they occasionally ate small crustaceans. Gladden et al. (1988), possibly summarizing the same data, also reported the species ate "fish and macro invertebrates" in the same study area. Twenty-four, 7-39 cm FL striped bass were also collected in the Raritan River during April 1976 - March 1977, but all of their stomachs were found empty (Lynch et al. 1977).

In general, most dietary studies of this species found seasonal and regional variability in prey (Table 23) that often reflected differences in local environmental conditions (e.g., salinity), in the size of the fish examined, and/or in the time of year (e.g., Bigelow and Schroeder 1953). There is a clear and well documented ontological shift in predation focus from small crustaceans (e.g., copepods, amphipods, and mysids) and small or juvenile fish for the youngest and smallest striped bass, to larger fish and crustaceans (e.g., crabs and shrimp) for the older and larger striped bass. The smaller-sized striped bass examined in the present survey ate a mix of small crustaceans and fish (Table 22).

Clearnose Skate (Raja eglanteria)

Hudson-Raritan Estuary Results

Clearnose skate were collected in the sandier, eastern polyhaline areas within the Estuary, such as Lower Bay, Gravesend Bay, East Bank, Romer Shoal, Sandy Hook Bay, and Raritan Channel (Strata 1, 3-6, 9; Figure 13), and during the summer (Wilk et al.1998). The diet of the 71 clearnose skate which were examined (range of 49.0-86.0 cm TL, mean of 63.3 cm) included a diversity of crustaceans, fish, and other prey (Table 24). Crangon, juvenile or small Atlantic rock crabs and Ovalipes ocellatus, and fish were most frequently found in the stomachs and contributed most to overall stomach volumes (Table 24). No empty stomachs were found.

Other prey or items found in clearnose skate stomachs in lesser quantities were: unidentified algae; mollusks (unidentified); amphipods (unidentified); mysids (Neomysis americana); decapod crustaceans (Pagurus longicarpus and juvenile Libinia sp.); and fish (unidentified juvenile hake, juvenile striped searobin, juvenile black sea bass, rock gunnel, juvenile searobins, and gobies).

Comparisons with Other Diet Studies

No previous studies of the diet of this species are known for this estuary. In fact, information on the diet of this species in general is very weak, and only available from a few studies (Table 25). In Delaware Bay, Fitz and Daiber (1963) examined the diet of this species and found that it also most commonly ate Crangon (i.e., an FO of 60%), Ensis directus (i.e., an FO of 36%), mud crabs (i.e., an FO of 20+%), and to a lesser degree, a variety of other small crustaceans, bivalve mollusks, and small fish such as weakfish and windowpane. Prey volume or weight contributions were not noted, but numerically, Crangon was still the dominant prey, and Neomysis was second in importance. Fritz and Daiber (1963) also noted that in the fall the skate ate more Neomysis, decapod crustaceans, and fish, but in the spring they focused more on Crangon and Ensis. Kimmel (1973) examined a small collection of juveniles (less than 44 cm TL) of this species at the mouth of Chesapeake Bay and found that Crangon, Ensis, and the mud shrimp Upogebia affinis volumetrically dominated stomach contents, but that a variety of epifaunal invertebrates (especially crustaceans) and small fish (searobins and hake) were also eaten. The diet described by the 1973 Kimmel paper is consistent with the prey that Hildebrand and Schroeder (1928) noted in the few clearnose skate that they examined from inside Chesapeake Bay. In the present study, the only prey that was found that have not been previously reported to be important in the diet were Atlantic rock crabs and O. ocellatus (Table 24 and Table 25).

Bluefish (Pomatomus saltatrix)

Hudson-Raritan Estuary Results

Juvenile, YOY (range of 7.0-13.5 cm FL, mean of 8.9 cm) bluefish were collected in the summer-fall in the Estuary, and mostly in or near channels (Figure 14; Wilk et al.1998). The stomachs of 63 bluefish were examined; 62 of these were from one collection August 1997. Fish, Crangon, and Neomysis dominated their diet (Table 26). The identifiable fish prey included mostly midwater forms: butterfish, silversides, anchovies, but also juvenile black sea bass.

The only other prey or items found in bluefish stomachs were unidentified algae and the polychaete Nereis succinea.

Comparisons with Other Diet Studies

Since only juvenile bluefish were collected and examined in this study, the following summary keeps that focus. Friedland et al.(1988) examined the diet of YOY bluefish in this estuary and reported that fish dominated the diet (by FO and TW) in Sandy Hook Bay (Stratum 1), especially bay anchovy, silversides, and killifish; however, Crangon were almost equally important, along with Neomysis. Breder (1922b) also notes that a small bluefish, also caught in Sandy Hook Bay, had a sand lance in its stomach. A limited study of the diet of bluefish in the Raritan River and adjacent western Raritan Bay found that juveniles (3-22.5 cm TL) collected by seine had eaten mummichog, bay anchovy, silversides, Crangon, Palaemonetes sp., and unidentified fish, while larger bluefish (greater than 37 cm FL) collected by gill net had eaten Atlantic menhaden, spot (Leiostomus xanthurus), bay anchovy, and Crangon (Lynch et al.1977).

In the adjacent brackish Hudson River, YOY bluefish consumed a variety of fish during their summer residency, including juvenile striped bass, white perch, American shad (Alosa sapidissima), blueback herring (A. aestivalis), Atlantic tomcod, silversides, bay anchovy, and occasionally other species, as well as blue crabs (Juanes et al.1993; Buckel et al.1999) (Table 27).

In nearby southern Long Island, New York, and elsewhere in the coastal Middle Atlantic Bight, juvenile bluefish were reported to commonly eat small schooling fish such as silversides, bay anchovy, butterfish, killifishes, juvenile Atlantic menhaden, herring, and weakfish, as well as benthic fish such as winter flounder, spot, and Atlantic tomcod (Table 27; Greenley 1939; Tatham et al.1984). Small crustaceans, such as Palaemonetes sp., Crangon, and Neomysis also dominated the YOY or juvenile bluefish diet (Table 27). The diet of the relatively small sampling of juvenile bluefish examined in the present study (Table 26) show that Friedland et al.'s (1988) findings are probably representative of the species' diet within the Estuary, are typical for this life stage of the species (Table 27), and are consistent with previous dietary summaries (Baird 1873; Nichols and Breder 1927; Hildebrand and Schroeder 1928; Bigelow and Schroeder 1953; Richards 1976).

Winter Skate (Raja ocellata)

Hudson-Raritan Estuary Results

Adult winter skate were collected from all areas of the Estuary during the cooler seasons, but they were especially abundant in or near channels (Figure 15; Wilk et al.1998). The 57 winter skate (range of 36.0-77.0 cm TL, mean of 55.8 cm) which were examined ate a diverse diet of benthic invertebrates and fish. Crangon was also a major item in the diet, both in terms of FO and TV. Other crustaceans and a variety of small or juvenile fish (e.g., Atlantic herring (Clupea harengus), sculpin, sand lance, and winter flounder) were also commonly consumed (Table 28).

Other prey or items found in winter skate stomachs in lesser quantities were: hydroids; nematodes (probably parasitic); gastropods (Nassarius trivittatus), bivalve mollusks (unidentified, Mulinia lateralis, and Ensis directus); polychaetes (unidentified); mysids (Neomysis); decapod crustaceans (unidentified crab fragments, Pagurus longicarpus, Dichelopandalus leptocerus, and juvenile blue crab); stomatopods (Squilla empusa); and fish (juvenile Atlantic herring, juvenile red hake, goby, unidentified juvenile sculpin, and smallmouth flounder).

Comparisons with Other Diet Studies

No previous studies of the diet of this species are known for this estuary.

Nichols and Breder (1927) and Bigelow and Schroeder (1953) noted the importance of Atlantic rock crabs and squid in the diet of this species in New England waters, and that this species also ate a variety of other benthic invertebrates (e.g., polychaetes, amphipods, shrimp, and razor clams) and small fish, such as juvenile skates, eels, herrings, smelt, sand lance, mackerel, butterfish, cunner, sculpins, and silver and Urophycis hake. The few available quantitative studies, including the present study, are consistent with this overview (Table 29), except that the present study shows a higher use of flounder as prey (Table 28).

Black Sea Bass (Centropristis striata)

Hudson-Raritan Estuary Results

There was a significant recruitment of juvenile black sea bass into the Estuary in the summer-fall of 1997. (Juveniles were rarely collected in other survey years, and adults were seldom found within the Estuary.) These juveniles were widespread in occurrence with a slight tendency to be found in or near channels (Figure 16; Wilk et al.1998). The August 1997 survey collected 46 juveniles 41 with nonempty stomachs (range of 2.9-29.0 cm TL, mean of 10.8 cm,), mostly at sites where colonies of redbeard sponge (Microciona prolifera) were collected. Various crustaceans dominated the diet, especially Crangon, Neomysis, and juvenile Atlantic rock crabs. The crustacean prey also included copepods, amphipods, isopods, and other small or juvenile decapods (Table 30). Several species of small or juvenile fish (e.g., cunner, goby, Atlantic menhaden, and possibly anchovy) were also eaten, as were some other benthic invertebrate taxa.

Other prey or items found in their stomachs in lesser quantities were: poriferans (unidentified); anthozoans (unidentified); nematodes (unidentified); gastropods (juvenile Crepidula sp.); bivalve mollusks (Ensis directus); polychaetes (unidentified and Asabellides oculata); copepods (unidentified and Pseudodiaptomus coronatus); isopods (Edotea triloba and Cirolana concharum); amphipods (Ericthonius sp., Stenothoe sp., and caprellids); decapod crustaceans (juvenile Ovalipes ocellatus and Pagurus sp.); and fish (goby, juvenile cunner, and unidentified).

Comparisons with Other Diet Studies

No previous studies of the diet of this species are known for this estuary.

In other Middle Atlantic Bight estuaries, juvenile black sea bass prey principally upon small benthic crustaceans such as isopods, amphipods, small mud crabs, Crangon, mysids, and copepods, and upon small fish such as northern pipefish, anchovies, and silversides (Hildebrand and Schroeder 1928; Bigelow and Schroeder 1953; Richards 1963; Kimmel 1973; Allen et al.1978; Festa 1979; Orth and Heck 1980; Werme 1981). Kimmel (1973) noted that polychaetes (e.g., Nereis sp. and Glycera sp.) can be important, too, and that the dominant prey shifted with fish growth (i.e., from small crustaceans such as Neomysis and various amphipods, to decapod crabs and polychaetes).

Most of the black sea bass collected in the Estuary were YOY and older juveniles (Wilk et al.1998), but adults in other coastal areas have been reported to feed upon a variety of epifaunal and infaunal invertebrates, especially crustaceans, squid, and small fish (Bigelow and Schroeder 1953; Richards 1963; Mack and Bowman 1983; Steimle and Figley 1996). The diet of the juvenile black sea bass examined in the Estuary was dominated by small crustaceans (Table 30) and was similar to the diet of the species reported in other studies (Table 31).

Spot (Leiostomus xanthurus)

Hudson-Raritan Estuary Results

Spot are generally found in the Estuary in the summer-fall, and were especially common in or near the Raritan Channel (Stratum 9) and Sandy Hook Bay (Stratum 1, Figure 17) (Wilk et al.1998). Forty-seven spot (range of 12.8-18.5 cm FL, mean of 15.4 cm) were collected in fall-winter 1996. The tube-dwelling amphipod Ampelisca abdita dominated the identifiable prey, but Crangon and Neomysis were also prominent. Other benthic invertebrates, including the copepod Pseudodiaptomus coronatus, constituted the rest of the stomach contents, which also contained a notable amount of unidentifiable organic matter or detritus (Table 32).

Other prey or items found in spot stomachs in lesser quantities were: green algae; bivalve mollusks (unidentified spat); polychaetes (unidentified); and amphipods (Corophium sp., Gammarus lawrencianus, and unidentified).

Comparisons with Other Diet Studies

No previous studies of the diet of this species are known for this estuary.

In southern New Jersey, Festa (1979) found that YOY spot ate copepods and amphipods (e.g., Ampelisca sp.), while larger juveniles also included a variety of polychaetes in the diet. Elsewhere, various studies show that YOY spot ate calanoid and harpacticoid copepods, a variety of other small crustaceans including larvae, and detritus; while larger juveniles (11-16 cm FL) ate more amphipods such as Ampelisca macrocephala (Table 33). Within Chesapeake Bay, Hildebrand and Schroeder (1928) reported that the species ate "small and minute crustaceans and annelids, together with smaller amounts of small mollusks, fish and vegetable debris". Smith et al.(1984) added that a wide diversity of plant material and benthic macrofauna was eaten. The diet of the spot examined from this estuary focused on small benthic organisms and detritus (Table 32), and is consistent with other dietary studies for the species (Table 33).

American Lobster (Homarus americanus)

Hudson-Raritan Estuary Results

A total of 47 American lobsters were collected during five seasons, mainly from Romer Shoal, Gravesend Bay, Chapel Hill, and Raritan Channel (Figure 18). The collections were a mix of juveniles and small adults (range of 2.8-9.9 cm carapace length, mean of 5.8 cm). The highly macerated state of the stomach contents, and the American lobster's known tendency to eat calcareous shell fragments, make identification of all true prey tentative. Species or items that could be identified from the diverse, particulate material in the stomach were included in this analysis, however. The dominant items evident in the stomachs were fragments of decapod crustaceans, especially Atlantic rock crabs, Pagurus sp., and Ovalipes ocellatus. Other items that were found suggest a range of taxa being eaten (i.e., hydroids to skate egg cases), as well as human artifacts such as coal pebbles, fragments of plastic and rubber, and synthetic fibers (Table 34).

Other prey or items found in American lobster stomachs in lesser quantities were: gastropods (Crepidula fornicata, Nassarius trivittatus, Lacuna vincta, Turbonilla sp., and Euspira operculums); bivalve mollusks (Mulinia lateralis); polychaetes (unidentified, Nereis succinea, and Spiochaetopterus oculatus); arachnids (juvenile Limulus polyphemus); cirripeds (Balanus sp.); decapod crustaceans (P. longicarpus, O. ocellatus, and juvenile Callinectes sp.); and echinoderms (Arbacia punctulata).

Comparisons with Other Diet Studies

No previous studies of the diet of this species are known for this estuary.

Steimle (1994) examined the diet of American lobster collected outside the mouth of this estuary. He reported that the diet varied among three collection sites that were variably influenced by sewage sludge disposal, and among bimonthly collections, although few American lobster were collected during winter. At the least-sludge-affected sites (probably being most appropriate for comparison with this estuary), the American lobsters were primarily eating Atlantic rock crabs, unidentified fish, the polychaete Pherusa affinis, and algae (Table 35). He also noted obvious human artifacts in the stomachs, especially animal hair and synthetic fibers.

In Long Island Sound, Weiss (1970) reported American lobsters also ate crustaceans, especially Atlantic rock crabs, mollusks such as Lacuna vincta and the blue mussel, and the polychaete Nereis virens. Other American lobster diet studies have been conducted outside the Middle Atlantic Bight area (e.g., in the sub-boreal Gulf of Maine and for Canadian populations). The diet of small American lobsters collected in the Estuary in the present study (Table 34) is consistent with the few available studies summarized in Table 35, and with the more general comments of Herrick (1911).

Tautog (Tautoga onitis)

Hudson-Raritan Estuary Results

Fifty-one tautog (range of 8.4-58.0 cm TL, mean of 37.5 cm) were collected and examined, primarily during the warmer seasons and from Romer Shoal, East Bank, Gravesend Bay, and, to a lesser degree, nearby areas (Figure 19). A variety of decapod crustaceans and mollusks were the most frequently eaten prey, with Atlantic rock crabs, xanthid crabs (including Dyspanopeus sayi), and blue mussels being prominent in the diet (Table 36).

Other prey or items found in tautog stomachs in lesser quantities were: hydroids; gastropods (unidentified, Crepidula sp., and unidentified eggs); bivalve mollusks (Anadara ovalis and juvenile northern quahogs); cirripeds (Balanus sp.); amphipods (Gammarus sp. and Ericthonius sp.); decapod crustaceans (unidentified and juvenile Libinia sp.); and shell hash.

Comparisons with Other Diet Studies

No previous studies of the diet of this species are known for this estuary, although Duffy-Anderson and Able (1999) mention that the diet of juvenile tautog held in cages in New York harbor appears to be "harpacticoid copepods, mysids, and amphipods."

Steimle and Shaheen (1999) summarized the diet of tautog, which has been resummarized in this report as Table 37. Dorf (1994) found that juveniles in Narragansett Bay, Rhode Island, ate various amphipods and copepods (mostly harpacticoids). Grover (1982) found a similar juvenile diet on the ocean side of Long Island, New York, as did Sogard (1992) in a southern New Jersey estuary. Nichols and Breder (1927) also noted seaweed in the diet of young tautog. The diet of older, 2-3 yr old juveniles was generally found to shift to mollusks, primarily blue mussels (Dorf 1994; Lankford et al.1995), but Festa (1979) reported mud crabs to be a primary item in the diet of larger juveniles in southern New Jersey.

Adult tautog are generally reported to prey primarily upon blue mussels, but also upon barnacles, crabs (Pagurus sp., Atlantic rock, and others), sand dollars (Echinarachnius parma), various amphipods, Crangon and other shrimp, American lobsters, scallops and other mollusks, and polychaetes (Hildebrand and Schroeder 1928; Bigelow and Schroeder 1953; Festa 1979; Steimle and Ogren 1982). Steimle (in review) found that besides blue mussels, the large anemone Metridium senile and razor clams (Ensis directus) can be important prey in Delaware Bay. The results of the present study (Table 36) reaffirm the importance of "shellfish," crustaceans, and mollusks, in the tautog diet.

Smooth Dogfish (Mustelis canis)

Hudson-Raritan Estuary Results

This relatively large (range of 55.0-111.0 cm TL, mean of 74.6 cm) visitor to the Estuary was collected in modest numbers (i.e., 42 specimens) during the warm seasons of both survey years, and mostly from Romer Shoal, East Bank, Gravesend Bay, nearby eastern Lower Bay areas, and near the Raritan Channel (Figure 20). It primarily ate a variety of decapod crustaceans and mollusks, and an occasional fish. Among the decapod prey, Crangon, Atlantic rock crabs, and Ovalipes ocellatus were commonly eaten, and the most notable molluscan prey was the razor clam Ensis directus (Table 38).

Other prey or items found in smooth dogfish stomachs in lesser quantities were: bivalve mollusks (Atlantic surfclam); cephalopods (unidentified squid); polychaetes (unidentified and Glycera sp.); decapod crustaceans (Pagurus pollicaris, Pagurus sp., and Libinia sp.); stomatopods (Squilla empusa); and fish (juvenile Atlantic menhaden, northern pipefish, and lined seahorse (Hippocampus erectus)).

Comparisons with Other Diet Studies

No previous studies of the diet of this species are known for this estuary.

Rountree and Able (1996) examined the diet of YOY of this species in a southern New Jersey estuary and found small Palaemonetes sp. and Crangon shrimp as the dominant prey, followed by unidentified polychaetes and crabs, blue crabs, and a variety of other benthic invertebrates (especially crustaceans); very few fish were eaten (Table 39). These results were similar to an early study, near Atlantic City, New Jersey, by Breder (1921) who reported that various crabs, eel grass, detritus, and fish were the most common items in the stomachs of smooth dogfish less than 64 cm TL. Nichols and Breder (1927) noted a preference for eating young American lobster and blue crabs, as well as other crustaceans, fish, and a variety of benthic macrofauna. Bigelow and Schroeder (1953) also commented on the potential heavy predation of smooth dogfish on American lobsters in Buzzards Bay, Massachusetts, as well as predation on Atlantic menhaden and tautog. Festa (1979) examined 12 juvenile smooth dogfish from southern New Jersey and found that blue crabs dominated (i.e., a TV of 91%) the diet, followed by "bay" [Crangon?] and Palaemonetes shrimp and juvenile weakfish. The present examination of the smooth dogfish diet in the Estuary (Table 38) shows that the species basically eats larger crustaceans and fish, which is consistent with the results of most other studies (Table 39).

Silver Hake (Merluccius bilinearis)

Hudson-Raritan Estuary Results

In general, silver hake were only collected as juveniles (range of 6.5-15.0 cm TL, mean of 10.1 cm) in the Estuary, and then primarily during the fall and in or near channels (Figure 21; Wilk et al.1998). Juvenile silver hake were not commonly available for examination except in November 1997 when 29 were collected. Crustaceans were the most common and important taxa in the diet, especially Crangon, Neomysis, Gammarus lawrencianus, and Ampelisca abdita, but small or juvenile fish were also eaten (e.g., silver hake, Atlantic menhaden, and probably anchovies). Both benthic and midwater fauna were eaten (Table 40).

Other prey or items found in silver hake stomachs in lesser quantities were: crustaceans (unidentified); cumaceans (unidentified); isopods (Edotea triloba); amphipods (unidentified, Jassa falcata, Hippomedon serratus, and Unciola sp.); decapod crustaceans (Palaemonetes sp.); and fish (juvenile Atlantic menhaden).

Comparisons with Other Diet Studies

No previous studies of the diet of this species are known for this estuary.

Table 41 summarizes dietary studies for juvenile and older silver hake that could be relevant to the present study. Schaefer (1960) and Steimle (1985) examined stomachs of this species collected just outside this estuary, and found that mysids (mostly Neomysis), Crangon, small unidentifiable fish, and YOY silver hake were the most important prey for near adult and adult fish. Schaefer (1960) also examined adults caught by hook-and-line on a surf-zone fishing pier in Long Branch, New Jersey (20 km south of the mouth of the Estuary), and found a slightly different diet from that found offshore. Inshore, he found that silver hake ate amphipods, Crangon, YOY silver hake, and mysids, in that order of relative importance. Richards (1963) reported a similar diet in Long Island Sound. On the continental shelf, Sedberry (1983) and Bowman et al.(1987) found that juvenile (i.e., less than or equal to 20 cm TL) silver hake ate various crustaceans, including euphausids and the hyperid amphipod Parathemisto gaudichaudi. Smaller, YOY silver hake (i.e., less than 5 cm TL) ate benthic and pelagic amphipods; larger YOY (i.e., between 5 and 10 cm TL) ate Crangon and Dichelopandalus pinguis [leptocerus?] shrimp, amphipods, small fish (sand lance and smaller silver hake), and squid. The juveniles collected in the Estuary during the present study ate a diet consistent with those studies noted in Table 41, with such studies as Jensen and Fritz (1960) and Vinogradov (1984), and with the generalizations of Bigelow and Schroeder (1953). Bowman et al. (1987) report that silver hake are mostly nocturnal feeders, and if so, mid-day collections might involve some loss of information by the digestion of softer prey. Few adult silver hake are collected in the Estuary (Wilk et al.1998).

Less Abundant Predators

The following predators were collected in lesser quantities and in more limited areas. Their diets are only briefly documented here, with identifiable prey being listed in order of their relative importance to overall stomach content volumes.

Fourspot Flounder (Paralichthys oblongus)

Forty-one examples of this predator were collected from several strata, and ranged between 6.7 and 33.0 cm TL (mean of 15.1 cm). Crangon, unidentified fish, Neomysis, and unidentified decapod crustacean zoeae were prominent in the diet.

Grubby (Myoxocephalus aenaeus)

Twenty-six specimens, ranging between 3.8 and 13.0 cm TL (mean of 7.9 cm), were collected mostly in the Lower Bay to East Bank area (Strata 3 and 5). They ate Crangon, Neomysis, juvenile Atlantic rock crabs, juvenile black sea bass, the tubiculous amphipod Corophium sp., the isopod Cyathura sp., caprellid amphipods, and the sand-tube worm Sabellaria vulgaris.

White Perch (Morone americana)

Twenty-one white perch were collected, mostly in western Raritan Channel (Stratum 9), and ranged between 16.0 and 27.7 cm TL (mean of 21.0 cm). These fish ate Crangon, unidentified small or juvenile fish, unidentified crustaceans, gobies (Gobisoma sp.), Neomysis, Palaemonetes sp., and Gammarus sp.

Northern Kingfish (Menticirrhus saxatilis)

Sixteen kingfish were collected, mostly in the Lower Bay to East Bank area (Strata 3 and 5), and ranged between 7.5 and 16.5 cm TL (mean of 10.9 cm). They ate Crangon, Gammarus lawrencianus, anchovies, unidentified polychaetes, unidentified crab, Neomysis, and Pagurus sp.

Smallmouth Flounder (Etropus microstomus)

Twelve specimens of this flounder were collected, mostly in the Lower Bay to East Bank area (Strata 3 and 5), and ranged between 11.3 and 15.0 cm TL (mean of 12.7 cm). These fish ate Crangon, Pagurus longicarpus, Neomysis, Pagurus sp., and Gammarus lawrencianus.

Spiny Dogfish (Squalus acanthias)

Twelve spiny dogfish were collected, mostly in the Romer Shoal and Ambrose Channel area (Strata 4 and 7), and ranged between 76.0 and 80.3 cm TL (mean of 77.4 cm). They ate unidentified fish, Atlantic rock crabs, juvenile ocean quahog, Pagurus pollicaris, Ovalipes ocellatus, and northern pipefish.

Atlantic Tomcod (Microgadus tomcod)

Eleven Atlantic tomcod were collected in the Gravesend and northern Lower Bay area (Strata 3 and 6), and ranged between 7.5 cm and 9.7 cm TL (mean of 8.7 cm). They ate Crangon and Gammarus lawrencianus.

Oyster Toadfish (Opsanus tau)

Ten toadfish were collected, mostly in Raritan Channel (Stratum 9), and ranged between 11.5 and 24.5 cm TL (mean of 16.1 cm). They ate Crangon, juvenile Atlantic rock crabs, Pagurus longicarpus, and unidentified fish.

Rock Gunnel (Pholis gunnellus)

Nine samples of this species were collected in the Lower Bay to East Bank area (Strata 3 and 5), and ranged between 5.2 and 12.3 cm TL (mean of 9.4 cm). They ate Neomysis, Photis sp., unidentified isopods, Leptocheirus pinguis, and unidentified copepods.

Cunner (Tautogolabrus adspersus)

Nine cunner were collected, mostly in the Sandy Hook Bay to East Bank area (Strata 4 and 5), and ranged between 3.2 and 12.2 cm TL (mean of 5.5 cm). Unidentified amphipods, harpacticoid copepods, Gammarus lawrencianus, Neomysis, Corophium sp., Ampelisca abdita, Ericthonius sp., unidentified foraminifera, and Unciola sp. were found in their stomachs.

Northern Puffer (Sphoeroides maculatus)

Eight puffer were collected in Sandy Hook Bay (Stratum 1), and ranged between 7.3 and 16.2 cm TL (mean of 10.0 cm). They ate the sand-tube worm Sabellaria vulgaris, Atlantic rock crabs, unidentified crabs, hydroids, Pagurus longicarpus, Ampelisca abdita, gastropod eggs, barnacles, algae, and wood fragments.

Atlantic Croaker (Micropogonias undulatus)

Four croaker were collected from Raritan Channel (Stratum 9), and ranged between 12.6 and 18.0 cm TL (mean of 15.6 cm). They ate Crangon, an unidentified clam, Ampelisca abdita, Neomysis, Glycera sp., and unidentified fish.

Longhorn Sculpin (Myoxocephalus octodecemspinosus)

Three specimens were collected from the East Bank-Ambrose Channel area (Strata 5 and 7), and ranged in length between 9.0 and 29.0 cm TL (mean of 22.2 cm). They ate sand lance, Crangon, unidentified fish, and juvenile Atlantic rock crabs.

Conger Eel (Conger oceanicus)

Three juvenile congers were collected (i.e., shaken out of discarded beverage containers brought up in the trawl) in Gravesend Bay (Stratum 6), and ranged between 20.5 and 30.2 cm TL (mean of 24.6 cm). They ate Pagurus longicarpus, juvenile Atlantic rock crabs, Crangon, and mud (xanthid) crabs.

Overall Perspective on Diets

The predator collection discussed in the preceding text appears representative of what is typically found within the Estuary. Wilk et al.(1998) listed 17 of the 20 predators examined in this dietary study as being among the most commonly collected species within the Estuary. The other species that they found to be common were pelagic or "forage" species such as bay anchovy, herrings, butterfish, and longfin inshore squid (Loligo pealeii) which are discussed subsequently. Three predators that were examined in this study, but that were not listed as the most common in the trawl survey, were smooth dogfish, tautog, and American lobster. These species were examined either because of their fishery importance (tautog and American lobster) or because of their being among the largest apex predators found within the Estuary (smooth dogfish).

The species occurring in the Estuary in the 1990s appear to be persistent since 1970s, i.e., the dominant species were consistent with those reported by Wilk and Silverman (1976). The fish community defined by Wilk et al.(1998) in this estuary is also similar, with a difference of only one or two dominant species, to that found in other larger Middle Atlantic Bight estuaries, e.g., Narragansett Bay, Rhode Island (Oviatt and Nixon 1973), Long Island Sound (Richards 1963), and Delaware Bay (Grimes 1983). However, as prey availability may differ in those estuaries, the diets discussed above may not adequately represent the situation for other estuaries.

Examination of diets from trawl-collected fish can involve biases related to the collection method. Some prey that were fresh and readily identified in the stomachs can be an artifact of within-trawl predation. This potential bias exists in most diet data based on trawl-caught samples, and is likely to involve the use of larger or motile epibenthic prey such as small fish, Crangon, and crabs that accumulate within the trawl's cod-end, or that are disturbed by the trawl doors, warps, footrope, or tickler chain to expose them to rapid-response predation. These results are also subject to other potential biases or errors that are typical of the method. For example, differential rates of prey digestion and stomach evacuation can be a bias, especially for afternoon collections (assuming diurnal predators often feed heavily in the morning), although American lobsters and other predators such as red hake are thought to be primarily nocturnal feeders.


Examination of the diets of common predators provides insight into the value of various estuarine prey and habitats to support fishery populations. Also, the conservation of the habitat of prey that can be essential to fishery resources is a requirement of the Magnuson-Stevens Fishery Conservation and Management Act (October 1996). Consequently, for those prey which were examined in this study and which were found to be eaten more commonly than others, a brief overview of their life histories and a discussion of their habitat use are presented to facilitate effective habitat management. The following section summarizes what is known of the life histories and habitat use of both the commonly eaten invertebrate prey as well as those fish that are less important to diets, but can be of interest to fishery management.

The prey that seem to be most widely used or to be eaten at the highest frequency or volume levels by one or more of the predators covered in the previous sections are summarized in Tables 42-44; Table 42 and Table 43 list nonfish used as prey, and Table 44 lists fish used as prey. These prey are listed in order of their overall importance as prey within the Estuary, based on the ranking of their percent frequency of occurrence in the diet or percent contribution to total stomach content volume, relative to the predators examined in this study.

Dominant Invertebrate Prey and Their Life Histories and Habitats

Sevenspine Bay Shrimp (Crangon septemspinosa)

The epibenthic, sevenspine bay shrimp (or sand shrimp) ranked first in importance to overall diet volumes for most of the predators. It was the most common prey of little skate, juvenile summer flounder, juvenile red hake, weakfish, spotted hake, striped and northern searobins, juvenile striped bass, clearnose and winter skates, juvenile black sea bass, silver hake, and fourspot flounder (Table 6, Table 10, Table 12, Table 14, Table 16, Table 18, Table 20, Table 24, Table 28, Table 30, and Table 40). Only winter flounder and tautog did not rely heavily on Crangon as prey, although it was occasionally eaten by both.

Crangon occurs on sandy to silty-sand sediments into which it can partially bury. It tolerates a wide range of salinity and temperatures, and occurs within estuaries and bays, offshore to about 90 m in depth, and from the sub-Arctic to Florida (Caracciolo and Steimle 1983). It is considered omnivorous, and will eat detritus, small invertebrates, and newly settled, postlarval fish such as flounder (Witting and Able 1993). It breeds throughout the warmer months, with prominent spring and weaker fall peaks known for some areas (Wehrtmann 1994). It can live for 2 yr and grow to about 7 cm TL.

Because Crangon is relatively motile and small, its abundance and distribution within the Estuary are not accurately known, although an unsuccessful effort was made to obtain such information (R. Reid, unpubl. data, National Marine Fisheries Serv., Highlands, NJ). It can avoid benthic grab samplers and pass through the mesh of standard trawls. Because of its importance to the diets of most fishery resources found in the Estuary, more should be known of its preferred habitats and sensitivity to human perturbation, including toxic chemical contaminant bioaccumulation. The species was also once found to be affected by "black spot disease," or chitinoclasia, within this estuary (Gopalan and Young 1975). The toxicity of chemically contaminated sediments in the Estuary to several crustacean species has been reported by Long et al.(1995), but tests were not conducted with Crangon, although tests on Palaemonetes pugio, a marsh dweller, were mentioned.

Neomysis americana

This mysid was generally second in overall importance, volumetrically, to diets. It was ranked first as prey for windowpane and second in overall importance to a variety of predators that focused upon Crangon as prey, except skates (Table 42). It was not found or identified in the diets of American lobster, tautog, and smooth dogfish in the size ranges examined in the present study.

Neomysis is a dominant component of the suprabenthic/planktonic community in most Middle Atlantic Bight estuarine ecosystems, but occurs widely along the Western Atlantic coast from Nova Scotia to the Caribbean Sea. Caracciolo and Steimle (1983) and Hargreaves (1995) report that it tolerates a wide range of salinities (i.e., from marine to as low as 1‰) and temperatures (i.e., from 0 to 25°C), and prefers to be over sandy sediment in depths less than 60 m. It occurs in swarms that are negatively phototaxic, and avoids strong light. It is omnivorous, eating mainly microalgae, zooplankton, and organic microdetritus. The abundance and distribution of Neomysis in the Estuary are unknown at present, but the species' photophobic nature suggests that deep channels and depressions in the Estuary with sandy sediments may be important daylight habitat, and when they may be most available as prey to demersal predators. As for Crangon, more needs to be known on Neomysis's distribution, habitat use, and sensitivity to human perturbations in this estuary.

Gammarus lawrencianus

This semipelagic amphipod (also called "scud") ranked third in overall importance, being found in 68% of the diets examined. It was especially important as prey to windowpane, juvenile scup, juvenile red hake, juvenile weakfish, spotted hake, northern searobin, juvenile silver hake, and northern kingfish (Table 42).

G. lawrencianus was reported by Bousfield (1973) to occur on or over sandy or muddy areas of estuarine areas of Southern New England. Amphipods of the genus Gammarus typically move across the bottom on their sides, and their laterally compressed body allows them to move readily within cracks and spaces among algae and other objects. At summer breeding times, a species of Gammarus was observed swarming in the evening at the water surface within the Estuary (Grant 1984), suggesting a period of enhanced exposure to predation. Little is known of the relative abundance and distribution of Gammarus in this estuary, but the species' association with vegetation and other shelter, as well as its semipelagic habits, make it difficult to survey. Sage and Herman (1972), in a rare reference to the genus in this estuary, found that G. fasciatus was only common in Sandy Hook Bay (Stratum 1) during November.

Atlantic Rock Crab (Cancer irroratus)

Juvenile or small Atlantic rock crabs were eaten by 60% of the predators, being most important to larger species such as little skate, striped searobin, summer flounder, clearnose skate, winter skate, American lobster, tautog, smooth dogfish, and to some juveniles such as those of black sea bass (Table 42). This prey was usually eaten in its YOY stage during the summer-fall, but soft-shelled stages of larger crabs were also eaten at all seasons.

The postmegalop, juvenile stages of this crab generally appear as part of the benthic macrofauna in early summer (Steimle and Stone 1973), and this coincides with their appearance in the diets of juvenile fish using this estuary (e.g., winter flounder, scup, summer flounder, and black sea bass; Table 2, Table 8, Table 10, Table 30) and in the diets of other small predators such as northern searobin (Table 20). Larger juvenile and small adult Atlantic rock crabs are eaten by other predators during other seasons; these larger crabs appear to leave this estuary in summer, except in deeper channels (Wilk et al.1998). Studies of this crab suggest that, despite its common name, "rock crab," it is more commonly found on sand bottoms than on gravel and rock (e.g., Jeffries 1966; Bigford 1979; Palma et al.1999). However, the use of rough bottom or rock habitats by motile invertebrates and fish is poorly known because of sampling problems and inadequate survey effort (Steimle and Zetlin 2000). Reilly and Saila (1978) used diver surveys and reported mussel beds as a preferred habitat for juvenile Atlantic rock crabs off Southern New England. Atlantic rock crabs were most commonly collected by trawl in and near channels and throughout the marine, eastern part of the Estuary (Figure 22).

Lady Crab (Ovalipes ocellatus)

The lady or calico crab is a warm-season (April-December) ecosystem component, being collected from all areas and strata (Figure 23), although it is reported to prefer sands (Stehlik et al.1991). Juveniles of this species were also most often found in diets. YOY seem to be available as prey in the summer and fall in this estuary, but larger (i.e., 20-30 mm) crabs were collected in the spring too (L. Stehlik, pers. comm., National Marine Fisheries Serv., Highlands, NJ).

Right-Handed Hermit Crabs (Pagurus spp.)

Several species of hermit crabs (Pagurus spp.) were eaten by predators (i.e., an overall FO of 64%), but these prey seemed only really important to American lobster and smallmouth flounder (Table 42). Usually only the distinct, distal ends of the legs and claws were identifiable in lobster stomachs. Two species were readily identified as prey, the small P. longicarpus and the larger P. pollicaris, the latter of which was rarely found as prey. Both species are considered omnivors/detritivors and are reported to be common on a wide range of habitats. P. longicarpus is found in shallow waters in the summer (including intertidal and lower salinity areas) from Canada to Texas, but migrates to deeper water and sandy bottoms as waters cool, where it often hibernates in pits that it digs (Rebach 1974). P. pollicaris tends to stay in deeper, more saline waters with sandy sediments.

Ampelisca abdita

This tube-dwelling amphipod was next in overall dietary importance, occurring in the diets of 56% of the predators examined. It was particularly important to the diets of winter flounder, windowpane, juvenile scup, juvenile weakfish, striped searobins, juvenile black sea bass, and juvenile silver hake (Table 42). Recent benthic surveys of this estuary (Cerrato et al.1989) found this species to be common throughout the year in silty areas such as Sandy Hook Bay (Stratum 1), in western areas of the Estuary (Strata 2 and 9), and in Gravesend Bay (Stratum 6). Considering this distribution, it is curious that Long et al.(1995) commented on tests of the toxicity of sediment from various locations within the Estuary to this species, and noted that, in the 1980s and early 1990s, western Raritan Bay silty sediments (western parts of Strata 2, 3, and 9) were found to be toxic, while sediments from sandy areas in the northeastern third of the Estuary (eastern part of Stratum 3, and Strata 4, 5, 7, and 8) were relatively low in toxicity. Wide variance in annual abundances have been reported for this species (Steimle and Caracciolo-Ward 1989).

Northern Quahog (Mercenaria mercenaria) and Atlantic Surfclam (Spisula solidissima) Siphons

This type of prey was important only to winter flounder, and was eaten infrequently by other predators (Table 42). Because winter flounder and these two clams are dominant and fishery important species within the Estuary, the clams are included in this discussion. Northern quahogs are generally found in the fine-sand, silty central, western, and southern areas of the Estuary (de Falco 1967; McCloy 1984; Cerrato et al.1989), basically in Strata 1-3 and 9, and in the deep silty area in Gravesend Bay (Stratum 6). Atlantic surfclams occur in the eastern, marine areas of the Estuary (Cerrato et al.1989), i.e., Strata 4-7. Thus, either one or the other of these two species of larger clams is available throughout the Estuary for siphon predation by winter flounder. The use of siphons seems unrelated to the availability of polychaetes and amphipods as potential prey, based on the results of Steimle and Caracciolo-Ward (1989) and Cerrato et al.(1989), who show that these taxa were generally available, although at lesser biomass levels during the winter, and at quantities comparable to those in other estuaries (Steimle and Caracciolo-Ward 1989). Predation on clam tissue would appear not to have any energetic advantage, as clam tissue has one-half to one-third of the caloric food-energy value of polychaetes or crustaceans (Steimle and Terranova 1985), and tearing off a piece of relatively tough and muscular siphon must entail more effort than picking up unattached prey off the sediment surface. Thus, this focused use of siphons seems to be an enigma, although it could be related to a declining supply of benthos in the fall, as is typically found in many estuaries and coastal areas (Steimle 1985, 1990). Brief habitat summaries of other, less-used prey are presented in Table 43.

Habitat and Community Associations of Invertebrate Prey

Habitat Associations

The invertebrate prey discussed in the preceding section come from one of three general habitat-associated groups within the Estuary: endobenthic, epibenthic, and suprabenthic (semipelagic). The endobenthic (or infaunal) prey group includes organisms living within the sediment or in tubes upon the sediment surface, and consists primarily of mollusks (often only their siphons being eaten), polychaetes, and certain amphipods such as Ampelisca abdita, Corophium sp., and Unciola sp. (Table 42). This prey group generally uses sediment carbon (including bacteria and meiofauna) or surficial phytoplankton as food. This group is exploited as prey by a limited group of predators: winter flounder, scup, and spot (Table 42).

The epibenthic prey group consists of mostly motile species, especially small decapod crustaceans that move slowly across the sediment surface (e.g., hermit, Atlantic rock, lady, and other crabs, and Crangon; Table 42). These prey tend to be omnivores, capable of using detritus as well as smaller organisms they encounter on the bottom, including larval fish (Witting and Able 1993). This group, especially Crangon, is exploited by the widest range of predators in this estuary.

The suprabenthic, or semipelagic, prey group consists primarily of Neomysis, seasonally augmented by gammarid amphipods such as Gammarus annulatus or G. lawrencianus, and by copepods that may be abundant near the bottom (e.g., Pseudodiaptomus coronatus). These prey typically occur in swarms, and Neomysis can spend the daytime close to the bottom, but move up in the water column at night. They tend to be planktivors, although the gammarids may be capable of exploiting a wider range of small food items, including the scavenging of carrion.

The high use of crustaceans as prey in all three of these habitat-associated groups seems to be typical of food webs in many estuaries, and has apparently not been significantly altered for decades in the Estuary, e.g., see Townes (1939). Townes (1939) also concludes that crustaceans are the most important prey of fish in New York coastal waters. He noted that "shrimp" (Crangon and Palaemonetes) and "opossum shrimp" (Neomysis) were the most important prey, but amphipods and other taxa were important, too.

Community Associations

Frame (1974), MacPhee (1969), and others have commented that the food of marine predators generally reflects the environmental conditions and habitats in which the predators live. Following is a brief review of where the aforementioned invertebrate prey can be expected to be found within the Estuary, based on available survey information. Because of logistic constraints, benthic invertebrate collections were not a feature of the 1996-97 survey. However, there have been several recent studies of the benthic community in the Estuary which have characterized the major community types and their distributions (Cerrato et al.1989; Steimle and Caracciolo-Ward 1989; Wilber et al., unpubl. data, National Ocean Serv., Charleston, SC).

Benthic organisms are known to exhibit wide variances in abundance, especially the smaller, short-lived species, but benthic communities, in general, are consistently associated with certain sediment characteristics and thus can be conservative over time, even if many community members fluctuate in abundance. Steimle and Caracciolo-Ward (1989) examined the information available on the Estuary's benthic community to the mid-1970s, Cerrato et al.(1989) examined the fauna in the mid-1980s, and Wilber et al.(unpubl. data, National Ocean Serv., Charleston, SC) examined the benthic fauna in the mid-1990s. All of these studies report both similarities and differences of major community types within the Estuary (as defined by dominant species), that are sediment and water depth related, for the most part.

Steimle and Caracciolo-Ward (1989) defined a silty sediment community numerically dominated by several species of polychaetes (e.g., spionids, Nephtys picta, and Sabellaria vulgaris), mollusks (e.g., Mulinia lateralis, Acteon punctostratus, Tellina agilis, and Nassarius trivittatus), and a few amphipods (e.g., Rhepoxynius epistomus). Examination of biomass data identified: 1) Nephtys incisa as important in muddy areas (such as Strata 1-2 and 6); 2) Glycera sp., Nassarius trivittatus, and Tellina agilis as important in Lower Bay sands (Strata 3 and 4); 3) Mulinia lateralis as important in Sandy Hook Bay (Stratum 1); and 4) Crangon, Pagurus sp., and Dyspanopeus sayi as important in scattered areas. These authors noted that this community may have been stressed from a severe tropical storm (hurricane Agnes) that passed through the area during the previous year.

Cerrato et al. (1989) found a different mix of common species in the same areas reported by Steimle and Caracciolo-Ward (1989). They noted dominant species and their general seasonal and spatial distributions; a majority of the benthic infaunal species that they found to be common in the mid-1980s were found to be numerically common prey items in the diets examined in the present study: Ampelisca abdita, Asabellides oculata, blue mussel spat, Crepidula fornicata, Corophium tuberculatum, northern quahogs, and Atlantic surfclams. This similarity of common infauna found by Cerrato et al.(1989) and common prey found in the present study suggests that the benthic community found in the mid-1980s persisted to the mid-1990 period of the diet survey. These benthic studies all reported that, overall, the benthic invertebrates within the Estuary were most abundant in a silty band that occurred: 1) from Sandy Hook Bay northwest to off Princes Bay, Staten Island (i.e., basically Stratum 1 and the deeper areas of Strata 2 and 3); 2) adjacent to Raritan Channel (Stratum 9); and 3) in areas of Gravesend Bay (Stratum 6). The species which were most abundant in this band included those which were prey, such as Ampelisca abdita, Asabellides oculata, C. tuberculatum, and northern quahogs. Overall, benthic invertebrates were least abundant in the eastern, fine-to-medium sand habitats of Strata 4 and 5, and the eastern parts of Stratum 3; the species found to be most common in these areas were blue mussel spat and Atlantic surfclams, which are also prey species.

The most recent benthic survey of the Estuary, during October 1994 and June 1995 (Wilber et al., unpubl. data, National Ocean Serv., Charleston, SC), noted the distribution of several benthic species that were primary prey in the present study; but their survey did not sample the channels (Strata 7-9). Atlantic surfclams and northern quahogs, the siphons of which were a major prey type for winter flounder, were most commonly collected in two separate areas of the Estuary: Atlantic surfclams within sandy Strata 4 and 5 and the northeastern third of Stratum 3, and northern quahogs in the silty parts of Strata 1 and 2 and lower half of Stratum 3. Blue mussels, a less common prey of several species, were collected in scattered locations across the eastern, sandy half of the Estuary, including near banks, shoals, and former borrow pits, in Strata 3-6. Blue mussels were especially common in June 1995, suggesting a strong spring 1997 recruitment occurred. The amphipod Ampelisca abdita was collected widely within the Estuary during both sampling periods, but especially in the silty parts of Strata 1-3 and 6, and irregularly in Strata 4 and 5.

The results of the most recent benthic studies by Cerrato et al. (1989) and Wilber et al. (unpubl. data, National Ocean Serv., Charleston, SC) are consistent, and suggest that certain recent benthic prey communities have persisted in their relative abundance and distribution within the Estuary. Their results are most likely representative of the prey community that would be available during this 1996-97 diet study, especially of those species that are relatively long lived such as the clams. There were, however, also benthic invertebrates they defined as abundant that did not appear in the present study to be readily used as prey: the minute capitellid "thread" worms Heteromastis filiformis and Mediomastus spp.; the spionid polychaete Streplospio benedicti; and the small bivalve mollusks softshell, Tellina agilis, Macoma baltica, Gemma gemma, and Mulinia lateralis. Steimle et al.(1994) found that winter flounder collected outside the Estuary often, but not always, ate what was most available (i.e., abundant and of a suitable size) in the benthic community.

Fish as Prey and Their Life Histories and Habitats

Fish are also eaten by a number of predators in the Estuary, especially by summer flounder, weakfish, spotted and silver hakes, striped bass, bluefish, and clearnose and winter skates (Table 10, Table 14, Table 16, Table 22, Table 24, Table 26, Table 28, and Table 40). The bay anchovy seems to be a favorite prey for many predators, but a number of demersal or benthic fish species are eaten frequently, too. It seems few juvenile or small fish are relatively immune from predation. None of the piscivors seem to be obligatory and almost all rely on epibenthic invertebrate prey to a high extent. Below is a summary of the fish observed in their stomachs, and some brief notes on habitats known to be commonly used by this prey group.

Twenty-six species of fish were identified in the stomachs of the predators examined in this study; other fish remains could not be identified to the species level (Table 44). Fish, at some level of identification, occurred in the diets of all but three predators, these exceptions being winter flounder, spot, and tautog. No specific fish species was widely eaten by predators. The maximum FO of prey among predators was 28% for anchovy being eaten by smallmouth flounder. Most fish that were found in the stomachs were juveniles, but some were mixed sizes, including adults of such small species as rock gunnel, northern searobin, smallmouth flounder, goby, northern pipefish, and lined seahorse. Most fishes eaten by predators were demersal, except anchovies, Atlantic menhaden, Atlantic herring, Alosa herring, Menidia sp., juvenile weakfish, butterfish, and possibly juvenile silver hake. Most fishes found in the Estuary seem to be preyed upon by larger fish, except elasmobranchs (i.e., skates and dogfish sharks), although fragments of skate egg cases (possibly empty) were found in some American lobster stomachs.

Following are some brief notes on the life history and habitat use of those fish most commonly eaten as prey, presented as a convenient reference for habitat managers involved in this estuary.

Searobins (Prionotus spp.)

All but the adults of the striped searobin were eaten by a number of predators, including incidences of cannibalism (Table 44). Able and Fahay (1998) reported that juveniles of both species prefer sandy sediments when they occur in estuaries during the late spring to fall, although northern searobin will move out of heated shallow waters to deeper, cooler water during mid-summer. Both species winter offshore.

Bay Anchovy (Anchoa mitchilli)

This is a common nektonic species and important prey for a variety of fish in this and other Middle Atlantic Bight estuaries (Houde and Zastrow 1991; Wilk et al.1998). It is a small, schooling species that feeds on zooplankton (including fish and decapod crustacean eggs and larvae), and tolerates a wide range of salinity and temperature, although its abundance and distribution within estuaries can vary annually (Houde and Zastrow 1991). It grows to about 9 cm TL, and can live for about 3 yr. Spawning begins at age 1 and occurs in the spring and summer. The eggs hatch in about 1 day, and the larvae and early juveniles are common in the summer/fall and can be an important prey for juvenile weakfish (e.g., Richards (1963), Van Engle and Joseph (1968), and others (Table 44)) and many other predators found in the Estuary. Wilk et al.(1998) show that, within the Estuary, bay anchovy was most frequently collected by trawls in Strata 1-3 (near Staten Island), 6, and channel Strata 8 and 9 (Figure 24), but were not found in the winter within this estuary.

Silver Hake (Merluccius bilinearis)

Although juveniles are commonly found within the Estuary during the cooler months (Wilk et al.1998), all life stages of this species were reported rare within central New Jersey estuaries (Able and Fahay 1998). This species is usually considered nektonic, but Auster et al. (1997) reported that juveniles of this species occur at high densities in patches of amphipod tubes and other complex, structured benthic habitats found on the continental shelf.

Cunner (Tautogolabrus adspersus)

This small species is usually found year-round in marine parts of estuaries, and associated with structure such as shellfish and seagrass/algal beds, piers, pilings, bridge abutments, rock rip-rap, etc., although it can be less common in the winter (Able and Fahay 1998). In the trawl survey of Wilk et al. (1998), smaller sizes of cunner, which usually occur in stomachs, were usually collected when the trawl picked up some large debris (such as automobile tires), snagged on some object on the bottom, or caught a quantity of redbeard sponge. This reliance on shelter and rough bottom, which interferes with trawling, can explain why the species has been reported to be rare in previous trawl surveys of the Estuary (Berg and Levinton 1985). Its occurrence in the stomachs of open-bottom predators, such as summer flounder and skate (Table 44), suggests that cunner can be available away from, but probably near, shelter at times.

Silverside (Menidia sp.)

This common "baitfish" is usually found over shallow, sandy, nearshore areas, but was only identified in juvenile bluefish stomachs (Table 44). Conover and Murawski (1982) report that the species will move out of estuaries during the fall-winter in the northern part of its range.

Winter Flounder (Pseudopleuronectes americanus)

Although not normally considered a prey species, juvenile winter flounder were relatively common in skate diets in this estuary (Table 44), and Manderson et al.(1999) found that a limited sampling of adult striped searobins suggested that juvenile winter flounder were preyed upon in shallow water of Sandy Hook Bay (Stratum 1). Many of the unidentified small flounder remains found in the stomachs examined in the present study (Table 44) may also be this species, although both windowpane and smallmouth flounder are found in this size range. This is a well studied, estuarine-coastal species (Pereira et al.1999), and its life history and habitat uses need not be reiterated here.

Sand Lance (Ammodytes sp.)

Able and Fahay (1998) reported that this species is common in shallow marine waters where it occurs in schools that often dive and burrow into sands when threatened. Skates appear to be its primary predator within the Estuary (Table 44). Sand lance were rarely collected in the recent trawl surveys within the Estuary (e.g., see Wilk et al.1998).

Butterfish (Peprilus triacanthus)

Able and Fahay (1998) summarized the life history and habitat use of this pelagic species which is found within estuaries during the summer, including the Hudson-Raritan (Wilk et al.1998). This species was collected from all survey strata, although collections were relatively scarce within Sandy Hook Bay (Stratum 1). Able and Fahay (1998) noted that this species is negatively phototaxic and stays near the bottom during the day, making it most accessible to demersal predators at that time. However, only the juveniles of bluefish and weakfish seem to eat it (Table 44). Early juveniles have been reported to be associated with and to accompany jellyfish when they appear inshore during the summer (Bigelow and Schroeder 1953).

American Eel (Anguilla rostrata)

Juveniles (elvers and "whips") of this eel were found in the stomachs of skate and adult spotted hake (Table 44). Able and Fahay (1998) reported that the juvenile and other phases of this species are common in estuaries, especially the Hudson River, where they occur in a wide range of habitats, silty to sandy, structured to unstructured.

Overall Perspective on Forage Base

Overall, the fish that were eaten as prey in this estuary were not as important as crustaceans and some other invertebrates as food for the bulk of the fish found in the Estuary. However, fish were a common prey type for some predators, and at times could have a notable impact on the survival and recruitment of some estuarine-dependent species. Understanding this relationship and its potential is important in developing a better understanding of the role of the benthic environment in fishery resource production.

Information on the diets of common fish and American lobster collected in the stressed Hudson-Raritan Estuary shows that these diets were still similar to the diets of the same species in other larger, less-stressed Middle Atlantic Bight estuaries. This suggests that the Estuary still functions tropho-dynamically like other, less-stressed areas. The study results also suggest that the Estuary's benthic habitat and macrofauna community are important to support a sustainable, multispecies fishery (and other biological resources such as wintering, fish-eating ducks). Steimle and Caracciolo-Ward (1989) and recent surveys all suggest that the Estuary's benthic fauna seem to be relatively healthy compared with other major estuaries, and that most of its expected community structure is still intact, although long-term trend data are absent. There could still be a potential problem with contamination of benthic prey by toxic substances from the Estuary's sediments and water, and from biotransfer up the food web, as suggested by Long et al. (1995).


We thank Barbara Lamp for supplying New Jersey Marine Academy of Science and Technology and other student volunteers, including Andy Craig. We also thank colleagues Eileen MacHaffie, Steve Fromm, Joe Vitaliano, and Bob Reid. The cooperation of the crew of the NOAA R/V Gloria Michelle (Eric Nelson, Jeff Broeneck, and Jeremy Adams), Sally Swarts of UNICOR-ADP, and Sue Fromm are also recognized. Mike Fahay assisted in the identification of juvenile fish, and Pat Shaheen provided support on copepod taxonomy. We also thank Jason Link and others for their constructive comments.


Able, K.W.; Fahay, M.P. 1998. The first year in the life of estuarine fishes in the Middle Atlantic Bight. New Brunswick, NJ: Rutgers University Press; 342 p.

Allen, D.M.; Clymer, J.P., III; Herman, S.S. 1978. Fishes of Hereford Inlet Estuary, southern New Jersey. Stone Harbor, NJ: Lehigh University and the Wetlands Institute; 138 p.

Auster, P.J.; Malatesta, R.J.; Donaldson, C.L.S. 1997. Distribution responses to small-scale habitat variability by juvenile silver hake, Merluccius bilinearis. Environ. Biol. Fishes 50:195-200.

Baird, S.F. 1873. Natural history of some of the more important food fishes of the south shore of New England. I. The scup, Stenotomus argyrops (Linn.) Gill. Bull. U.S. Comm. Fish Fish. 1:228-252.

Barans, C.A. 1969. Distribution, growth and behavior of the spotted hake in the Chesapeake Bight. [M.S. thesis.] Williamsburg, VA: Coll. of William and Mary; 53 p.

Bason, W.H.; Allison, S.E.; Horseman, L.O.; Keirsey, W.H.; LaCivita, P.E.; Sander, R.D.; Shirey, C.A. 1976. Fishes. In: Ecological studies in the vicinity of the proposed Summit Power Station, January-December 1975. Vol. 1. Ithaca, NY: Ichthyological Associates; 392 p.

Bason, W.H.; Allison, S.E.; Horseman, L.O.; Keirsey, W.H.; Shire, C.A. 1975. Fishes. In: Ecological studies in the vicinity of the proposed Summit Power Station, January-December 1974. Vol. 1. Ithaca, NY: Ichthyological Associates; 327 p.

Berg, D.L.; Levinton, J.S. 1985. The biology of the Hudson-Raritan Estuary, with emphasis on fishes. NOAA Tech. Memo. NOS OMA 16; 170 p.

Bharadwaj, A.S. 1988. The feeding ecology of the winter flounder Pseudopleuronectes americanus (Walbaum) in Narragansett Bay, Rhode Island. [M.S. thesis.] Kingston, RI: Univ. of Rhode Island; 129 p.

Bigelow, H.B.; Schroeder, W.C. 1953. Fishes of the Gulf of Maine. Fish. Bull. (Wash., D.C.) 53; 577 p.

Bigford, T.E. 1979. Synopsis of biological data on the rock crab, Cancer irroratus Say. NOAA Tech. Rep. NMFS Circ. 426; 26 p.

Bousfield, E.L. 1973. Shallow-water gammaridean Amphipoda of New England. Ithaca, NY: Comstock Publ.; 312 p.

Bowman, R.E.; Azarovitz, T.R.; Howard, E.S.; Hayden, B.P. 1987. Food and distribution of juveniles of seventeen Northwest Atlantic fish species, 1973-1976. NOAA Tech. Mem. NMFS-F/NEC-45; 57 p.

Boynton, W.R.; Polgar, T.T.; Zion, H.H. 1981. Importance of juvenile striped bass feeding habits in the Potomac Estuary. Trans. Am. Fish. Soc. 110:56-63.

Breder, C.M., Jr. 1921. The food of Mustelus canis (Mitchill) in mid-summer. Copeia 1921(101):85-86.

Breder, C.M., Jr. 1922a. Observations on young bluefish. Copeia 1922(106):34-36.

Breder, C.M., Jr. 1922b. The fishes of Sandy Hook Bay. Zoologia II(15):330-341.

Buckel, J.A., Conover, D.O., Steinberg, N.D., McKown, K.A. 1999. Impact of age-0 bluefish (Pomatomus saltatrix) predation on age-0 fishes in the Hudson River estuary: evidence for density-dependent loss of juvenile striped bass (Morone saxatilus). Can. J. Fish. Aquat. Sci. 56:275-287.

Burr, B.M.; Schwartz, F.J. 1986. Occurrence, growth, and food habits of the spotted hake, Urophycis regia, in the Cape Fear Estuary and adjacent Atlantic Ocean, North Carolina. Northeast Gulf Sci. 8(2):115-127.

Caracciolo, J.V.; Steimle, F.W. 1983. An atlas of the distribution and abundance of dominant benthic invertebrates in the New York Bight apex with reviews of their life histories. NOAA Tech. Rep. NMFS SSRF-766; 58 p.

Carlson, J.K. 1991. Trophic relationships among demersal fishes off New Haven Harbor (New Haven, CT) with special emphasis on the winter flounder (Pseudopleuronectes americanus). [M.S. thesis.] New Haven, CT: Southern Connecticut State Univ.; 71 p.

Cerrato, R.M.; Bokuniewicz, H.J.; Higgins, M.H. 1989. A spatial and seasonal study of the benthic fauna of the Lower Bay of New York Harbor. State Univ. N.Y. - Stony Brook Mar. Sci. Res. Cent. Spec. Rep. 84 (Ref. 89-1); 325 p.

Chao, L.N.; Musick, J.A. 1977. Life history, feeding habits, and functional morphology of juvenile sciaenid fishes in the York River Estuary, Virginia. Fish. Bull. (Wash., D.C.) 75:657-702.

Chee, P.K. 1977. Feeding ecology of black sea bass Centropristis striata on an artificial reef off Virginia. [M.S. thesis.] Norfolk, VA: Old Dominion Univ.; 51 p.

Conover, D.; Cerrato, R.; Bokuniewicz, H. 1985. Effects of borrow pits on the abundance and distribution of fishes in the Lower Bay of New York Harbor. State Univ. N.Y. - Stony Brook Mar. Sci. Res. Cent. Spec. Rep. 64 (Ref. 85-20); 95 p.

Conover, D.O.; Murawski, S.A. 1982. Offshore winter migration of the Atlantic silverside, Menidia menidia. Fish. Bull. (Wash., D.C.) 80:145-150.

Curran, H.W.; Reis, D.T. 1937. Fisheries investigations in the lower Hudson River. In: Biological survey of the lower Hudson watershed. Albany, NY: New York Conservation Dep.; p.124-145.

de Falco, P. 1967. A report on the shellfish resources of Raritan Bay, New Jersey. App. A. Report of the Conference on the Pollution of Raritan Bay and Adjacent Interstate Waters. Metuchen, NJ: U.S. Dep. of the Interior, Federal Water Pollution Control Admin., Northeast Reg.; p. 653-681.

de Sylva, D.P.; Kalber, F.A., Jr.; Shuster, C.N. 1962. Fishes and ecological conditions in the shore zone of the Delaware River Estuary, with notes on other species collected in deeper waters. Univ. Del. Mar. Lab. Inf. Ser. Publ. 5; 164 p.

Dorf, B.A. 1994. Ecology of juvenile tautog (Tautoga onitis) in Narragansett Bay, Rhode Island. [Ph.D. dissertation.] Kingston, RI: Univ. of Rhode Island; 213 p.

Duffy-Anderson, J.T.; Able, K.W. 1999. Effects of municipal piers on the growth of juvenile fishes in the Hudson River Estuary: a study across a pier edge. Mar. Biol. (Berlin) 133:409-418.

Eigenmann, C.H. 1902. Investigations into the history of the young squeteaque. Bull. U.S. Fish Comm. 21:45-51.

Fay, C.W.; Neves, R.J.; Pardue, G.B. 1982. Species profile: life histories and environmental requirements of coastal fishes and invertebrates (Mid-Atlantic) -- striped bass. U.S. Fish Wildl. Serv. FWS/OBS-82/11.8 and U.S. Army Corps Eng. TR EL-82-4; 36 p.

Festa, P.J. 1979. The fish forage base of the Little Egg Harbor Estuary. N.J. Bur. Fish. Tech. Rep. 24 M; 271 p.

Field, I.A. 1907. Unutilized fishes and their relation to the fishing industries. U.S. Bur. Fish. Doc. 622; 50 p.

Fitz, E.S., Jr.; Daiber, F.C. 1963. An introduction to the biology of Raja eglanteria Bosc 1803 and Raja erinacea Mitchill 1825 as they occur in Delaware Bay. Bull. Bingham Oceanogr. Collect. Yale Univ. 18(3):9-96.

Frame, D.W. 1974. Feeding habits of young winter flounder (Pseudopleuronectes americanus): prey availability and diversity. Trans. Am. Fish. Soc. 103:261-269.

Friedland, K.D.; Garman, G.C.; Bedja, A.J.; Studholme, A.F.; Olla, B. 1988. Interannual variation in diet and condition in juvenile bluefish during estuarine residency. Trans. Am. Fish. Soc. 117:474-479.

Gardinier, M.N.; Hoff, T.B. 1982. Diet of striped bass in the Hudson River Estuary. N.Y. Fish Game J. 29(2):152-165.

Gelsleichter, J.; Musick, J.A.; Nichols, S. 1999. Food habits of the smooth dogfish, Mustelus canis, dusky shark, Carcharhinus obscurus, Atlantic sharpnose shark, Rhizoprionodon terraenovae, and the sand tiger, Carcharias taurus, from the Northwest Atlantic Ocean. Environ. Biol. Fishes 54:205-217.

Gilbert, W.H.; Suchow, E.F. 1977. Predation by winter flounder (Pseudopleuronectes americanus) on the siphons of the clam, Tellina agilis. Nautilus 91(1):16-17.

Ginsberg, I. 1952. Flounder of the genus Paralichthys and related genera in American waters. Fish. Bull. (Wash., D.C.) 52:267-351.

Gladden, J.B.; Cantelmo, F.R.; Croom , J.M.; Shapot, R. 1988. Evaluation of the Hudson River ecosystem in relation to the dynamics of fish populations. Am. Fish. Soc. Monogr. 4:37-52.

Gopalan, U.K.; Young, J.S. 1975. Incidence of shell disease in shrimp in the New York Bight. Mar. Poll. Bull. 6 (10):149-153.

Gosner, K.L. 1973. Guide to identification of marine and estuarine invertebrates, Cape Hatteras to the Bay of Fundy. New York, NY: Wiley-Interscience; 693 p.

Grant, D. 1984. Scud spawning. Underwater Nat. 15(1):25.

Grant, G.C. 1962. Predation of bluefish on young Atlantic menhaden in Indian River, Delaware. Chesapeake Sci. 3:45-47.

Grecay, P.A. 1990. Factors affecting spatial patterns of feeding success and condition of juvenile weakfish (Cynoscion regalis) in Delaware Bay: field and laboratory assessment. [M.S. thesis.] Lewes, DE: Univ. of Delaware; 193 p.

Greenley, J.R. 1939. Fishes and habitat conditions of the shore zone based upon July and August seining investigations. In: A biological survey of the salt waters of Long Island, 1938 (Part II). N.Y. Conserv. Dep. Annu. Rep. 15(Suppl.):72-91.

Grimes, C.B. 1983. Nekton (finfish). In: Sharp, J.H., ed. The Delaware Estuary: research as background for estuarine management and development. New Castle, DE: Delaware River and Bay Authority; p. 169-182.

Grover, J.J. 1982. The comparative feeding ecology of five inshore, marine fishes off Long Island, New York. [M.S. thesis.] New Brunswick, NJ: Rutgers Univ.; 197 p.

Hall, A. 1894. Notes on the oyster industry of New Jersey. In: Report of the U.S. Commission of Fish and Fisheries for 1892. Washington, DC: U.S. Government Printing Off.; p. 463-528.

Hargreaves, B.R. 1995. Mysid crustaceans. In: Dove, L.E.; Nyman, R.M., eds. Living resources of the Delaware Estuary. Philadelphia, PA: U.S. Environmental Protection Agency; p. 59-68.

Hartman, K.J.; Brandt, S.B. 1995. Trophic resource partitioning, diets, and growth of sympatric estuarine predators. Trans. Am. Fish. Soc. 124:520-537.

Herrick, F.H. 1911. Natural history of the American lobster. Bull. U.S. Bur. Fish. 29:149-408.

Hickey, C.R., Jr. 1975. Fish behavior as revealed through stomach content analysis. N.Y. Fish Game J. 22:148-155.

Hildebrand, S.F.; Schroeder, W.C. 1928 . Fishes of Chesapeake Bay. Fish. Bull. (Wash., D.C.) 43; 388 p.

Hollis, E.H. 1952. Variations in the feeding habits of the striped bass, Roccus saxatilis (Walbaum), in Chesapeake Bay. Bull. Bingham Oceanogr. Collect. Yale Univ. 14(1):111-131.

Homer, M.; Boynton, W.R. 1978. Stomach analysis of fish collected in the Calvert Cliffs region, Chesapeake Bay -- 1977. Univ. Md. Chesapeake Biol. Lab. Ref. 78-154-CBL; 360 p.

Houde, E.D.; Zastrow, C.E. 1991. Bay anchovy Anchoa mitchilli. In: Funderburk, S.L.; Mihursky, J.A.; Jordan, S.J.; Riley, D., eds. Habitat requirements for Chesapeake Bay living resources. 2nd ed. Annapolis, MD: U.S. Environmental Protection Agency; p 8.1-8.14.

Irlandi, E.A.; Mehlich, M.E. 1996. The effect of tissue cropping and disturbance by browsing fishes on growth of two species of suspension-feeding bivalves. J. Exp. Mar. Biol. Ecol. 197:279-293.

Jeffries, H.P. 1966. Partitioning of the estuarine environment by two species of Cancer. Ecology 47:477-481.

Jensen, A.C.; Fritz, R.L. 1960. Observations on the stomach contents of silver hake. Trans. Am. Fish. Soc. 89(2):239-240.

Juanes, F.; Conover, D.O. 1994. Rapid growth, high feeding rates and early piscivory in young-of-year bluefish, Pomatomus saltatrix. Can. J. Fish. Aquat. Sci. 51:1752-1761.

Juanes, F.; Marks, R.E.; McKown, K.A.; Conover, D.O. 1993. Predation by age-0 bluefish on age-0 anadromous fishes in the Hudson River Estuary. Trans. Am. Fish. Soc. 122:348-356.

Keirsey, W.H.; Shirey, C.A.; Sander, R.D.; Domermuth, R.B.; Bason, W.H.; LaCivita, P.E.; Charles, K.E.; Henrick., M.R. 1977. Fishes. In: Ecological studies in the vicinity of the proposed Summit Power Station, January-December 1976. Vol. 1. Ithaca, NY: Ichthyological Associates; 463 p.

Kimmel, J.J. 1973. Food and feeding of fishes from Magothy Bay, VA. [M.S. thesis.] Williamsburg ,VA: Old Dominion Univ.; 220 p.

Kurtz, R.J. 1975. Stomach content analysis in relation to difference in growth rates of winter flounder (Pseudopleuronectes americanus) for two Long Island bays. [M.S. thesis.] Greenvale, NY: Long Island Univ.; 60 p.

Langton, R.W.; Bowman, R.E. 1981. Food of eight Northwest Atlantic pleuronectiform fishes. NOAA Tech. Rep. NMFS SSRF-749; 16 p.

Lankford, T.E.; Davis, J.; Wilbur, A.E.; Targett, T.E. 1995. Predation by juvenile tautog Tautoga onitis on blue mussels Mytilus edulis: ontogenetic changes in feeding capability and behavioral tendencies. [Abstr.] Paper presented at: American Fisheries Society 125th Annual Meeting; Tampa, FL; Aug. 27-31, 1995; p. 75.

Lascara, J. 1981. Fish predator-prey interactions in areas of eelgrass (Zostera marina). [M.A. thesis.] Williamsburg, VA.: Coll. of William and Mary; 81 p.

Lawler, Matusky & Skelly Engineers. 1980. Stomach content analysis. In: Biological and water quality data collected in the Hudson River near the proposed Westway Project during 1979-1980. Vol. II. Albany, NY: New York State Department of Transportation.

Linton, E. 1901. Parasites of fishes of the Woods Hole region. Bull. U.S. Fish Comm. 19:405-492.

Linton, E. 1921. Food of young winter flounders. U.S. Dep. Comm. Bur. Fish. Doc. 907; 14 p.

Long, E.R.; Wolfe, D.A.; Scott, K.J.; Thursby, G.B.; Stern, E.A.; Peven, C.; Schwartz, T. 1995. Magnitude and extent of sediment toxicity in the Hudson-Raritan Estuary. NOAA Tech. Memo. NOS ORCA-88; 230 p.

Luczkovich, J.J.; Olla, B.L. 1983. Feeding behavior, prey consumption, and growth of juvenile red hake. Trans. Am. Fish. Soc. 112:629-637.

Lux, F.E.; Porter, L.R., Jr.; Nichy, F. 1996. Food habits of winter flounder in Woods Hole Harbor. Northeast Fish. Sci. Cent. Ref. Doc. 96-02; 18 p.

Lynch, J.M.; Byrne, D.M.; Ashton, D.E.; Allen, B.M.; Heyl, A.; Markowski, R.; Woithe, T.W. 1977. Impingement and entrainment at the Sayreville Generating Station and a study of the fishes of the Raritan River near the station, April 1976 - March 1977. Ithaca, NY: Ichthyological Associates; 318 p.

Mack, R.G., Jr.; Bowman, R.E. 1983. Food and feeding of black sea bass (Centropristis striata). Woods Hole Lab. Ref. Doc. 83-45; 20 p.

MacKenzie, C.L. 1992. Fisheries of Raritan Bay. New Brunswick, NJ: Rutgers University Press; 304 p.

MacPhee, G.K. 1969. Feeding habits of winter flounder Pseudopleuronectes americanus (Waldbaum) as shown by stomach content analysis. [M.A. thesis.] Boston, MA: Boston Univ.; 66 p.

Manderson, J.P.; Phelan, B.A.; Bejda, A.J.; Stehlik, L.L.; Stoner, A.W. 1999. Predation by striped searobin (Prionotus evolans, Triglidae) on young-of-the-year winter flounder (Pseudopleuronectes americanus, Walbaum): examining size selection and prey choice using field observations and laboratory experiments. J. Exp. Mar. Biol. Ecol. 242:211-231.

Mann, J.M. 1974. Some aspects of the biology of the searobins Prionotus carolinus and Prionotus evolans. [M.S. thesis.] Greenvale, NY: Long Island Univ.; 37 p.

Markle, D.F.; Grant, G.C. 1970. The summer food habits of young-of-the-year striped bass in three Virginia rivers. Chesapeake Sci. 11(1):50-54.

Marshall, N. 1946. Observations on the comparative ecology and life history of two searobins, Prionotus carolinus and Prionotus evolans strigatus. Copeia 1946(3):118-144.

McCloy, T.W. 1984. Draft report on the shellfish resources of the Raritan Bay complex. Trenton, NJ: New Jersey Division of Fish, Game, and Wildlife; 20 p.

McEachlan, J.D.; Boesch, D.F.; Musick, J.A. 1976. Food division within two sympatric species-pair of skates (Pisces: Rajidae). Mar. Biol. (Berlin) 35:301-317.

Medcoff, J.C.; MacPhail, J.S. 1952. The winter flounder -- a clam enemy. Fish. Res. Board Can. Atl. Biol. Stat. Note 118:3-8.

Merrill, F.J.H. 1904. Higher Crustacea of New York City. N.Y. State Mus. Bull. 91(Zool. 12):117-189.

Merriman, D. 1941. Studies on the striped bass (Roccus saxatilis) of the Atlantic coast. Fish. Bull. (Wash., D.C.) 50:1-77.

Michelman, M.S. 1988. The biology of juvenile scup (Stenotomus chrysops (L.)) in Narragansett Bay, R.I.: food habits, metabolic rate and growth rate. [M.S. thesis.] Kingston, RI: Univ. of Rhode Island; 106 p.

Moore, E. 1947. Studies on the marine resources of Southern New England. VI. The sand flounder, Lophosetta aquosa (Mitchill); a general study of the species with special emphasis on age determination by mean of scales and otoliths. Bull. Bingham Oceanogr. Collect. Yale Univ. 11(3):1-79.

Mulkana, M.S. 1966. The growth and feeding habits of juvenile fishes in two Rhode Island estuaries. Gulf Res. Rep. 2:97-167.

National Ocean Service. 1994. Tidal current tables; 1995; Atlantic Coast of North America.

National Ocean Service. 1995. New York Harbor; Navigational chart #12327 (27th ed.).

Nichols, J.T.; Breder, C.M., Jr. 1927. The marine fishes of New York and Southern New England. Zoologica 9(1):1-192.

NJDEP [New Jersey Department of Environmental Protection]. 1975. Survey of aquatic organisms -- Caven Point Cove, Hudson River. Port Republic, NJ: New Jersey Division of Fish, Game, and Shellfisheries; 7 p.

O'Brien, L.; Burnett, J.; Mayo, R.K. 1993. Maturation of nineteen species of finfish off the northeast coast of the United States, 1985-1990. NOAA Tech. Rep. NMFS 113; 66 p.

Olla, B.L.; Bedja, A.J.; Martin, A.D. 1974. Daily activity, movements, feeding, and seasonal occurrences in the tautog, Tautoga onitis. Fish. Bull. (Wash., D.C.) 72:27-35.

Orth, R.J.; Heck, K.L, Jr. 1980. Structural components of eelgrass (Zostera marina) meadows in the lower Chesapeake Bay -- fishes. Estuaries 3:278-288.

Oviatt, C.A.; Nixon, S.W. 1973. The demersal fish of Narragansett Bay: an analysis of community structure, distribution and abundance. Estuarine Coastal Mar. Sci. 1:361-378.

Palermo, M.; Ebersole, B.; Peyman-Dove, L.; Lashlee, D.; Wisemiller, B.; Houston, L.; Will, R. 1998. Dredged materials management plan (DMMP) for the port of New York and New Jersey -- siting of island CDFs and constructed CAD pits. [Draft rep.] New York, NY: U.S. Army Corps of Engineers; 43 p. + app.

Palma, A.T.; Steneck, R.S.; Wilson, C.J. 1999. Settlement-driven, multiscale demographic patterns of large benthic decapods in the Gulf of Maine. J. Exp. Mar. Biol. Ecol. 241:107-136.

Pearcy, W.G. 1962. Ecology of an estuarine population of winter flounder, Pseudopleuronectes americanus (Walbaum). Bull. Bingham Oceanogr. Collect. Yale Univ. 18(1):1-78.

Peck, J.I. 1896. The source of marine food. Bull. U.S. Fish Comm. 15:351-368.

Pereira, J.J.; Goldberg, R.; Ziskowski, J.J.; Berrien, P.L.; Morse, W.W.; Johnson, D.L. 1999. Essential fish habitat source document: winter flounder, Pseudopleuronectes americanus, life history and habitat characteristics. NOAA Tech. Memo. NMFS-NE-138; 39 p.

Pihl, L.; Baden, S.P.; Diaz, R.J.; Schaffner, L.C. 1992. Hypoxia-induced structural changes in diet of bottom-feeding fish and Crustacea. Mar. Biol. (Berlin) 112:349-361.

Poole, J.C. 1964. Feeding habits of the summer flounder in Great South Bay. N.Y. Fish Game J. 11:28-34.

Rachlin, J.W.; Warkentine, B.E. 1987. Dietary preference of the spotted hake, Urophycis regia, from the inner New York Bight. Ann. N.Y. Acad. Sci. 494:434-437.

Rachlin, J.W.; Warkentine, B.E. 1988. Feeding preference of sympatric hake from the inner New York Bight. Ann. N.Y. Acad. Sci. 529:157-159.

Rebach, S. 1974. Burying behavior in relation to substrate and temperature in the hermit crab, Pagurus longicarpus. Ecology 55:195-198.

Reilly, P.N.; Saila, S.B. 1978. Biology and ecology of the rock crab, Cancer irroratus, Say, 1817, in Southern New England waters (Decapoda, Brachyura). Crustaceana 34:121-140.

Richards, S.W. 1963. The demersal fish population on Long Island Sound. Bull. Bingham Oceanogr. Collect. Yale Univ. 18(2):1-101.

Richards, S.W. 1976. Age, growth, and food of bluefish (Pomatomus saltatrix) from east-central Long Island Sound from July through November 1975. Trans. Am. Fish. Soc. 105:523-525.

Richards, S.W.; Mann, J.M.; Walker, J.A. 1979. Comparison of spawning seasons, age, growth rates, and food of two sympatric species of searobins, Prionotus carolinus and Prionotus evolans, from Long Island Sound. Estuaries 2:255-268.

Richards, S.W.; Merriman, D.; Calhoun, L.H. 1963. Studies on the marine resources of Southern New England. IX. The biology of the little skate, Raja erinacea Mitchill. Bull. Bingham Oceanogr. Collect. Yale Univ. 18(3):5-65.

Rountree, R.A.; Able, K.W. 1992. Foraging habits, growth, and temporal patterns of salt-marsh creek habitat use by young-of-year summer flounder in New Jersey. Trans. Am. Fish. Soc. 121:765-776.

Rountree, R.A.; Able, K.W. 1996. Seasonal abundance, growth, and foraging habits of juvenile smooth dogfish, Mustelus canis, in a New Jersey estuary. Fish. Bull. (Wash., D.C.) 94:522-534.

Sage, L.E.; Herman, S.S. 1972. Zooplankton of the Sandy Hook Bay area, N.J. Chesapeake Sci. 13(1):29-39.

Scarlett, P.G. 1986. Life history investigations of marine fish: occurrence, movements, food habits and age structure of winter flounder from select New Jersey estuaries. N.J. Bur. Mar. Fish. Tech. Ser. 86-20; 57 p.

Scarlett, P.G. 1988. Life history investigations of marine fish: occurrence, movements, food habits, and age structure of winter flounder from selected New Jersey estuaries. N.J. Bur. Mar. Fish. Tech. Ser. 88-20; 46 p.

Scarlett, P.G.; Giust, L.M. 1989. Results of stomach content analysis of selected finfish collected in the Manasquan River, 1984-86. [Federal Aid to Fisheries Project F-15-R-30 rep.] Trenton, NJ: New Jersey Division of Fisheries and Wildlife; 44 p.

Schaefer, R.H. 1960. Growth and feeding habits of the whiting or silver hake in the New York Bight. N.Y. Fish Game J. 7(2):85-98.

Schaefer, R.H. 1970. Feeding habits of striped bass from the surf waters of Long Island. N.Y. Fish Game J. 17:1-17.

Sedberry, G.R. 1983. Food habits and trophic relationships of a community of fishes on the outer continental shelf. NOAA Tech. Rep. NMFS SSRF-773; 56 p.

Shuster, C.N., Jr. 1959. A biological evaluation of the Delaware River Estuary. Univ. Del. Mar. Lab. Inf. Ser. Publ. 5; 77 p.

Smith, F.E. 1950. The benthos of Block Island Sound. I. The invertebrates, their quantities and relations to the fishes. [Ph.D. dissertation.] New Haven, CT; Yale Univ.; 213 p.

Smith, R.W.; Daiber, F.C. 1977. Biology of summer flounder, Paralichthys dentatus, in Delaware Bay. Fish. Bull. (Wash., D.C.) 75:823-830.

Smith, S.M.; Hoff, J.G.; O'Neil, S.P.; Weinstein, M.P. 1984. Community and trophic organization of nekton utilizing shallow marsh habitats, York River, Virginia. Fish. Bull. (Wash., D.C.) 82:455-467.

Sogard, S.M. 1992. Variability in growth rates of juvenile fishes in different estuarine habitats. Mar. Ecol. Prog. Ser. 85: 35-53.

Squibb, K.S.; O'Connor, J.M.; Kneip, T.J. 1991. New York/New Jersey Harbor Estuary Program Module 3.1: toxic characterizations. [Draft rep.] Philadelphia, PA: U.S. Environmental Protection Agency; 67 p.

Stehlik, L.L.; MacKenzie, C.L., Jr.; Morse, W.W. 1991. Distribution and abundance of four brachyuran crabs on the Northwest Atlantic shelf. Fish. Bull. (Wash., D.C.) 89:473-492.

Stehlik, L.L.; McMillan, D.G.; Pikanowski, R.A.; MacHaffie, E.M.; Wilk, S.J. (In preparation). Crabs at the crossroads: blue, rock, and lady crabs in the Hudson-Raritan estuary.

Stehlik, L.L.; Meise, C.J. 2000. Diet of winter flounder in a New Jersey estuary: ontogenic change and spatial variation. Estuaries 23:381-391.

Steimle, F.W. 1985. Biomass and estimated productivity of the benthic macrofauna in the New York Bight: a stressed coastal area. Estuarine Coastal Shelf Sci. 21:539-554.

Steimle, F.W. 1990. Benthic macrofauna and habitat monitoring on the continental shelf of the Northeast United States. I. Biomass. NOAA Tech. Rep. NMFS 86; 28 p.

Steimle, F.W. 1994. Sewage sludge disposal and winter flounder, red hake, and American lobster feeding in the New York Bight. Mar. Environ. Res. 37:233-256.

Steimle, F.W.; Caracciolo-Ward, J.V. 1989. A reassessment of the status of the benthic macrofauna of the Raritan Estuary. Estuaries 12:145-156.

Steimle, F.W.; Figley, W. 1996. The importance of artificial reef epifauna to black sea bass diets in the Middle Atlantic Bight. N. Am. J. Fish. Manage. 16:433-439.

Steimle, F.W.; Jeffress, D.; Fromm, S.A.; Reid, R.N.; Vitaliano, J.J.; Frame, A. 1994. Predator-prey relationships of winter flounder, Pseudopleuronectes americanus, in the New York Bight apex. Fish. Bull. (Wash., D.C.) 92:608-619.

Steimle, F.W.; Ogren, L. 1982. Food of fish collected on artificial reefs in the New York Bight and off Charleston, South Carolina. Mar. Fish. Rev. 44(6-7):49-52.

Steimle, F.W.; Shaheen, P.A. 1999. Tautog (Tautoga onitis) life history and habitat requirements. NOAA Tech. Memo. NMFS-NE-118; 23 p.

Steimle, F.W.; Stone, R.B. 1973. Abundance and distribution of inshore benthic fauna off southeastern Long Island, New York. NOAA Tech. Rep. NMFS SSRF-673; 50 p.

Steimle, F.W.; Terranova, R.J. 1985. Energy equivalence of organisms on the continental shelf of the Northwest Atlantic. J. Northwest Atl. Fish. Sci. 6:117-124.

Steimle, F.W.; Terranova, R.J. 1991. Trophodynamics of select demersal fishes in the New York Bight. NOAA Tech. Memo. NMFS-F/NEC-84; 11 p.

Steimle, F.W.; Zetlin, C. 2000. Reef habitats in the Middle Atlantic Bight: abundance, distribution, associated biological communities, and fishery resource use. Mar. Fish. Rev. 62(2):24-42.

Steiner, W.W.; Luczovich, J.J.; Olla, B.L. 1982. Activity, shelter usage, growth and recruitment of juvenile hake, Urophycis chuss. Mar. Ecol. Prog. Ser. 21:539-554.

Tatham, T.R.; Thomas, D.L.; Danilla, D.J. 1984. Fishes of Barnegat Bay, New Jersey. In: Kennish, M.J.; Lutz, R.A., eds. Ecology of Barnegat Bay, New Jersey. New York, NY: Springer-Verlag; p. 241-280.

Thomas, D.L. 1971. The early life history and ecology of drum (Sciaenidae) in the lower Delaware River, a brackish tidal estuary. Ichthyol. Assoc. Bull. 3:1-247.

Timmons, M. 1995. Relationships between macro algae and juvenile fishes in the inland bays of Delaware. [Ph.D. dissertation.] Lewes, DE: Univ. of Delaware; 155 p.

Townes, H.K., Jr. 1939. Ecological studies on the Long Island marine invertebrates of importance as fish food or as bait. In: A biological survey of the salt waters of Long Island, 1938 (Part I). N.Y. Conserv. Dep. Annu. Rep. 14(Suppl.):163-176.

Tracy, H.C. 1910. Annotated list of fishes known to inhabit the waters of Rhode Island. In: 40th annual report of the Commission of Inland Fisheries. Providence, RI: Commission of Inland Fisheries; p. 35-176.

Tressler, W.L.; Bere, R. 1939. A quantitative study of the plankton of the bays of Long Island. In: A biological survey of the salt waters of Long Island, 1938 (Part I). N.Y. Conserv. Dep. Annu. Rep. 14(Suppl.):177-191.

Turgeon, D.D.; Quinn, J.F.; Bogan, A.E.; Coan, E.V.; Hochberg, F.G.; Lyons, W.G.; Mikkelsen, P.M.; Neves, R.J.; Roper, C.F.E.; Rosenberg, G.; Roth, B.; Scheltema, A.; Thompson, F.G.; Vecchione, M.; Williams, J.D. 1998. Common and scientific names of aquatic invertebrates from the United States and Canada: mollusks. 2nd ed. Am. Fish. Soc. Spec. Publ. 26; 509 p.

Van Engle, W.A.; Joseph, E. 1968. Characterization of coastal and estuarine fish nursery grounds as natural communities. [Final rep.; Commercial Fisheries Research and Development Act grant] Richmond, VA: Virginia Commission on Fisheries; 43 p.

Vinogradov, V.I. 1984. Food of silver hake, red hake and other fishes of Georges Bank and adjacent waters, 1968-74. Northwest Atl. Fish. Organ. Sci. Counc. Stud. 7:87-94.

Warkentine, B.E.; Rachlin, J.W. 1988. Analysis of the dietary preference of the sand flounder, Scophthalmus aquosus, from the New Jersey coast. Ann. N.Y. Acad. Sci. 529:164-166.

Wehrtmann, I.S. 1994. Larval production of the caridean shrimp, Crangon septemspinosa, in waters adjacent to Chesapeake Bay in relation to oceanographic conditions. Estuaries 17:509-518.

Weiss, H.M. 1970. The diet and feeding behavior of the lobster, Homarus americanus, in Long Island Sound. [Ph.D. dissertation.] New Haven, CT; Univ. of Connecticut; 80 p.

Weiss, H.M. 1995. Marine animals of Southern New England and New York -- identification keys to common nearshore and shallow water macrofauna. Conn. Dep. Environ. Protect. Bull. 115; 19 sections.

Welsh, W.W.; Breder, C.M, Jr. 1924. Contributions to life histories of Sciaenidae of the eastern United States coast. Fish. Bull. (Wash., D.C.) 39:141-201.

Werme, C.E. 1981. Resource partitioning in a salt marsh community. [Ph.D. dissertation.] Boston, MA: Boston Univ.; 131 p.

Wilk, S.J.; Pikanowski, R.A.; McMillan, D.G.; MacHaffie, E.M. 1998. Seasonal distribution and abundance of 26 species of fish and megafauna collected in the Hudson-Raritan Estuary, January 1992 - December 1997. Northeast Fish. Sci. Cent. Ref. Doc. 98-10; 145 p.

Wilk, S.J.; Silverman, M.J. 1976. Summer benthic fish fauna of Sandy Hook Bay, New Jersey. NOAA Tech. Rep. NMFS SSRF-698; 16 p.

Williams, A.B.; Abele,.L.G.; Felder, D.L.; Hobbs, H.H.; Manning, R.B.; McLaughlin, P.A.; Perez Farfante, I. 1988. Common and scientific names of aquatic invertebrates from the United States and Canada: decapod crustaceans. Am. Fish. Soc. Spec. Publ. 17; 77 p.

Witting, D.A.; Able, K.W. 1993. Effects of body size on probability of predation for juvenile summer and winter flounder based on laboratory experiments. Fish. Bull. (Wash., D.C.) 91:577-581.

Wolfe, D.A.; Long, E.R.; Thursby, G.B. 1996. Sediment toxicity in the Hudson-Raritan Estuary: distribution and correlations with chemical contamination. Estuaries 19:901-912.

Worobec, M.N. 1984. Field estimate of daily ration of winter flounder, Pseudopleuronectes americanus (Walbaum) in a Southern New England salt pond. J. Exp. Mar. Biol. Ecol. 77:183-196.

DO =
dissolved oxygen
ES =
empty stomachs
FL =
fork length
FO =
mean percent frequency of occurrence
index of relative importance
mean percent contribution to total stomach content dry weight
TL =
total length
TN =
mean percent contribution to total number of individual items in the stomach
TV =
mean percent contribution to total stomach content volume
TW =
mean percent contribution to total stomach content weight
young of the year
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